Approval and Promulgation of Federal Implementation Plan for Oil and Natural Gas Well Production Facilities; Fort Berthold Indian Reservation (Mandan, Hidatsa, and Arikara Nation), North Dakota, 17835-17864 [2013-05666]
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Vol. 78
Friday,
No. 56
March 22, 2013
Part III
Environmental Protection Agency
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40 CFR Part 49
Approval and Promulgation of Federal Implementation Plan for Oil and
Natural Gas Well Production Facilities; Fort Berthold Indian Reservation
(Mandan, Hidatsa, and Arikara Nation), North Dakota; Rule
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Federal Register / Vol. 78, No. 56 / Friday, March 22, 2013 / Rules and Regulations
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 49
[EPA–R08–OAR–2012–0479; FRL–9789–3]
Approval and Promulgation of Federal
Implementation Plan for Oil and
Natural Gas Well Production Facilities;
Fort Berthold Indian Reservation
(Mandan, Hidatsa, and Arikara Nation),
North Dakota
Environmental Protection
Agency (EPA).
ACTION: Final rule.
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AGENCY:
SUMMARY: The EPA is taking final action
to promulgate a Reservation-specific
Federal Implementation Plan in order to
regulate emissions from oil and natural
gas production facilities located on the
Fort Berthold Indian Reservation in
North Dakota. The Federal
Implementation Plan includes basic air
quality regulations for the protection of
communities in and adjacent to the Fort
Berthold Indian Reservation. The
Federal Implementation Plan requires
owners and operators of oil and natural
gas production facilities to reduce
emissions of volatile organic
compounds emanating from well
completions, recompletions, and
production and storage operations. This
Federal Implementation Plan will be
implemented by the EPA, or a delegated
tribal authority, until replaced by a
Tribal Implementation Plan. The EPA
proposed a Reservation-specific Federal
Implementation Plan concurrently with
an interim final rule on August 15,
2012. This final Federal Implementation
Plan replaces the interim final rule in all
intents and purposes on the effective
date of the final rule. The EPA is taking
this action pursuant to the Clean Air Act
(CAA).
DATES: This final rule is effective on
April 22, 2013.
ADDRESSES: The EPA has established a
docket for this action under Docket ID
No. EPA–R08–OAR–2012–0479. All
documents in the docket are listed on
the www.regulations.gov Web site.
Although listed in the index, some
information is not publicly available,
i.e., CBI or other information whose
disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available either electronically through
www.regulations.gov, or in hard copy at
the Air Program, Environmental
Protection Agency (EPA), Region 8,
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1595 Wynkoop Street, Denver, Colorado
80202–1129. The EPA requests that if at
all possible, you contact the individual
listed in the FOR FURTHER INFORMATION
CONTACT section to view the hard copy
of the docket. You may view the hard
copy of the docket Monday through
Friday, 8 a.m. to 4 p.m., excluding
federal holidays.
FOR FURTHER INFORMATION CONTACT:
Deirdre Rothery, U.S. Environmental
Protection Agency, Region 8, Air
Program, Mail Code 8P–AR, 1595
Wynkoop Street, Denver, Colorado
80202–1129, (303) 312–6431,
rothery.deirdre@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document, ‘‘we’’, ‘‘us’’,
and ‘‘our’’ refer to the EPA.
Definitions
For the purpose of this document, we are
giving meaning to certain words or initials as
follows:
i. The initials APA mean or refer to the
Administrative Procedure Act.
ii. The words or initials Act or CAA mean or
refer to the Clean Air Act, unless the
context indicates otherwise.
iii. The initials BTU mean or refer to British
Thermal Unit.
iv. The initials CAFOs mean or refer to
Consent Agreement Final Orders.
v. The initials CDPHE mean or refer to
Colorado Department of Public Health
and Environment Air Pollution Control
Division.
vi. The initials CO mean or refer to carbon
monoxide.
vii. The words EPA, we, us or our mean or
refer to the United States Environmental
Protection Agency.
viii. The words Reservation or the initials
FBIR mean or refer to the Fort Berthold
Indian Reservation.
ix. The initials FIP mean or refer to Federal
Implementation Plan.
x. The initials GOR mean or refer to gas-tooil ratio.
xi. The initials LACT mean or refer to lease
automatic custody transfer.
xii. The initials MDEQ mean or refer to
Montana Department of Environmental
Quality.
xiii. The initials NAAQS mean or refer to the
National Ambient Air Quality Standards.
xiv. The initials NAICS mean or refer to the
North American Industry Classification
System.
xv. The initials NDDoH mean or refer to the
North Dakota Department of Health.
xvi. The initials NDIC mean or refer to the
North Dakota Industrial Commission.
xvii. The initials NESHAP mean or refer to
National Emission Standards for
Hazardous Air Pollutants.
xviii. The initials NMED mean or refer to
New Mexico Environment Department
Air Quality Bureau.
xix. The initials NOX mean or refer to
nitrogen oxides.
xx. The initials NO2 mean or refer to nitrogen
dioxide.
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xxi. The initials NSPS mean or refer to New
Source Performance Standards.
xxii. The initials NSR mean or refer to new
source review.
xxiii. The initials ODEQ mean or refer to
Oklahoma Department of Environmental
Quality Air Quality Division.
xxiv. The initials PM mean or refer to
particulate matter.
xxv. The initials PSD mean or refer to
prevention of significant deterioration.
xxvi. The initials PTE mean or refer to
potential to emit.
xxvii. The initials RCT mean or refer to
Railroad Commission of Texas, Oil and
Gas Division.
xxviii. The initials SCADA mean or refer to
Supervisory Control and Data
Acquisition.
xxix. The initials SIP mean or refer to State
Implementation Plan.
xxx. The initials SO2 mean or refer to sulfur
dioxide.
xxxi. The initials TAR mean or refer to Tribal
Authority Rule.
xxxii. The initials TAS mean or refer to
treatment as state.
xxxiii. The initials TIP mean or refer to Tribal
Implementation Plan.
xxxiv. The initials UDEQ mean or refer to
Utah Department of Environmental
Quality.
xxxv. The initials VOC mean or refer to
volatile organic compound(s).
xxxvi. The initials VRU mean or refer to
vapor recovery unit.
xxxvii. The initials WDEQ mean or refer to
Wyoming Department of Environmental
Quality Air Quality Division.
Table of Contents
I. Background
II. Basis for Final Action
III. Final Action
IV. Major Issues Raised by Commenters and
EPA’s Response
A. Purpose and Scope of FIP
B. Legal Basis and Authority
C. Rule Development and Implementation
D. Applicability
E. Control Equipment and Requirements
F. Monitoring and Recordkeeping
Requirements
G. Reporting Requirements
H. Cost Analysis
I. Public Notice
V. Summary of Final Rule and Significant
Changes From the Proposed and Interim
Final Rule
A. Administrative Edits
B. Introduction
C. Compliance Schedule
D. Provisions for Delegation of
Administration to the Three Affiliated
Tribes of the Mandan, Hidatsa, and
Arikara Nation
E. General Provisions
F. Construction and Operational Control
Measures
G. Control Equipment Requirements
H. Monitoring Requirements
I. Recordkeeping Requirements
J. Reporting Requirements
K. Effect on Permitting of Facilities
L. Registration Requirements
VI. Statutory and Executive Order Reviews
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Federal Register / Vol. 78, No. 56 / Friday, March 22, 2013 / Rules and Regulations
I. Background
On August 1, 2012, we signed a
proposed rulemaking to establish a
Federal Implementation Plan (FIP) for
oil and natural gas production facilities
located on the Fort Berthold Indian
Reservation (FBIR). We also signed an
interim final rule concurrent with the
proposed action because we found good
cause under Section 553(b)(B) of the
Administrative Procedure Act, 5 U.S.C.
551 et seq. that notice-and-comment are
impracticable, unnecessary or contrary
to the public interest in this instance.
The proposal and concurrent interim
final rule were published in the Federal
Register on August 15, 2012 (77 FR
48878), and residents of the FBIR, as
well as industry representatives and
environmental groups commented on
the proposed rule. During the 60-day
comment period that ended on October
15, 2012, we also held a public hearing
in New Town, North Dakota on
September 12, 2012. We received seven
written comments during the comment
period and 12 people provided oral
testimony at the public hearing. This
Federal Register action announces our
final action on the proposed regulations.
In promulgating this rule, the EPA is
exercising its discretionary authority
under Sections 301(a) and 301(d)(4) of
the Clean Air Act (CAA) to promulgate
regulations as necessary to protect tribal
air resources. Promulgating this final
rule addresses an important initial step
to fill a regulatory gap between state and
federal requirements with regard to
controlling volatile organic compound
(VOC) emissions from oil and natural
gas operations on the FBIR. There is no
other federal rule, including the recently
finalized New Source Performance
Standards (NSPS) and National
Emissions Standards for Hazardous Air
Pollutants (NESHAP) for the Oil and
Natural Gas Sector (NSPS OOOO and
NESHAP HH),1 that establishes
regulations for the particular oil and
natural gas production operations that
exist on the FBIR. This is in contrast to
oil and natural gas operations off the
Reservation, which are governed by the
North Dakota Department of Health
(NDDoH) regulations and North Dakota
Industrial Commission (NDIC)
regulations within the State of North
Dakota’s jurisdiction. The NDDoH
requirements were developed with an
understanding of the high VOC
1 ‘‘Oil and Natural Gas Sector: New Source
Performance Standards and National Emission
Standards for Hazardous Air Pollutants Review,
Final Rule’’ Federal Register 77:159 (16 August
2012) p. 49490. The regulations can be accessed at
https://www.epa.gov/airquality/oilandgas/
actions.html and are included in the docket for this
rule.
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emissions and infrastructure constraints
that exist in the region. Consistent with
the regulatory structure that exists off
the FBIR, and NSPS OOOO, this rule
has requirements for VOC emissions
control and reductions, monitoring,
recordkeeping, and reporting. This rule
also establishes requirements that are
clear and legally and practicably
enforceable.
We developed this rule in
consultation with the Three Affiliated
Tribes of the Mandan, Hidatsa, and
Arikara Nation. As part of this
consultation, we evaluated the oil and
natural gas activities and sources of
VOC emissions that could impact air
resources on the Reservation and the
differences in the VOC emission
reduction requirements for those
facilities operating on the FBIR
compared to those facilities operating in
NDDoH jurisdiction. The final rule we
are promulgating today establishes
regulations for oil and natural gas
production and storage operations
specific to the FBIR and applies to all
lands on the FBIR, which is defined by
the Act of March 3, 1891 (26 Statute
1032) and which includes all lands
added to the Reservation by Executive
Order of June 17, 1982.
We drafted the requirements that are
consistent to the greatest extent
practicable with the most relevant
aspects of neighboring state and local
rules concerning the air pollutant
emitting activities on the FBIR. We do
not intend, nor do we expect, this
regulation to impose significantly
different regulatory burdens upon
industry or the residents of the FBIR
than those imposed by the rules of state
and local air agencies in the
surrounding areas. We evaluated the
regulations imposed by other oil and
natural gas producing state
jurisdictions, NDDoH, NDIC, and NSPS
OOOO. Included in the docket for this
rule are copies of the regulations and
guidance that we considered in this
process, as well as a technical support
document 2 (TSD) explaining the
requirements.
We requested comments on all
aspects of our proposed action and
provided a 60-day comment period.
During the comment period, we
received comments on our proposed
rule that supported our proposed action
and that were critical of our proposed
action. After evaluating all the
comments that were received, we are
taking final action to respond to the
2 The Technical Support Document includes a
more detailed explanation of the development of
this FIP. It can be found in the docket for this rule,
Docket ID: EPA–R08–OAR–2012–0479, which can
be accessed at: https://www.regulations.gov.
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comments we have received, explain the
basis for our action, and promulgate the
final rule. In this final rule, also referred
to as the Federal Implementation Plan
for Oil and Natural Gas Well Production
Facilities; Fort Berthold Indian
Reservation (Mandan, Hidatsa, and
Arikara Nation), North Dakota, we are
making certain revisions based on the
information provided by commenters
and regulated entities. This preamble to
the final rule responds to the issues
raised by commenters and describes the
final rule and significant changes from
the proposed rule.
II. Basis for Final Action
This Federal Register action
announces the EPA’s final action on the
proposed regulations of August 15,
2012. In promulgating this rule, the EPA
is exercising its discretionary authority
under Sections 301(a) and 301(d)(4) of
the CAA to promulgate such
implementation plan provisions as are
necessary or appropriate to protect air
quality within the FBIR, specifically
identified in 40 CFR part 49, subpart
K—Implementation Plans for Tribes—
Region VIII. After evaluating air quality
issues for the FBIR, the EPA was
concerned that there was a gap in air
quality requirements for oil and natural
gas production facilities on the FBIR
under the CAA and its implementing
regulations.
Our proposed rule in August 2012
was generally based upon the aspects of
neighboring NDIC and NDDoH
regulations most relevant to the oil and
natural gas production VOC-emitting
activities occurring on the FBIR. We
acknowledged that there were some
differences between the requirements in
the proposed rule and those in the NDIC
and NDDoH regulations, most notably
additional monitoring requirements.
These differences were necessary to
meet the standards for promulgating
FIPs. Included in the docket for the
proposed rulemaking were copies of all
of the state rules that the EPA
considered in this process, as well as a
TSD comparing the proposed
regulations with the state regulations
and a description of why the EPA
believed the proposed rule was
appropriate.
During the public comment period, a
number of FBIR residents, industry
representatives and the regulated
entities, environmental and resident
advocate organizations, and tribal
government agencies submitted
comments on the rule proposed by the
EPA and offered suggestions for
improving the proposed rule. We have
fully considered all substantive public
comments on our proposal and have
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concluded that certain changes are
warranted. Those changes are discussed
in Section V of this notice. However, the
EPA does not intend, nor does it expect,
these regulations to impose significantly
different regulatory burdens upon
industry or the residents within the
FBIR than those imposed by the rules of
the NDIC and NDDoH in the
surrounding areas.
III. Final Action
In this action, we are promulgating a
Reservation-specific FIP to establish
enforceable control requirements for
reducing VOC emissions from oil and
natural gas production activities on the
FBIR in North Dakota. This final rule
replaces the interim final rule
promulgated on August 15, 2012 (77 FR
48878) in all intents and purposes on
the effective date of the final rule.
IV. Major Issues Raised by Commenters
and EPA’s Response
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A. Purpose and Scope of FIP
Comment: Multiple commenters
described the ways in which the
existing oil and natural gas development
had negatively affected their
communities. For example, commenters
described black smoke, visible soot, and
strong gas odors. Other commenters
expressed support of the EPA’s decision
to cover existing wells in the FIP.
Response: We acknowledge the
concerns expressed by the commenters
related to oil and natural gas production
activities on the FBIR. The purpose of
this FIP, in part, is to address the
potential impacts of VOC emissions
caused by the oil and natural gas
production occurring in the region. By
requiring process equipment at oil and
natural gas production facilities to be
operated with specific air emission
controls, under specific operating
conditions and following specific
procedures, this FIP will help address
these concerns. We are requiring that
operations at these facilities be
monitored and records be kept such that
any improper process or emission
control equipment operated by the
owner or operator at a facility can be
identified and remedied by the EPA
through enforcement of this FIP. The
public can report possible harmful
environmental activity on the EPA’s
Web site at https://www.epa.gov/tips/.
We acknowledge the commenters
support of the FIP to cover existing
wells. As discussed in the TSD, one goal
of this FIP was to provide an avenue of
compliance with the CAA for those
companies subject to CAFO agreements.
Our primary goal, as always is with
regard to regulations developed under
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the CAA, was to ensure increased
protection to the public health and the
environment. This FIP provides these
benefits through promulgation of
enforceable requirements to limit VOC
emissions from facilities that
constructed prior to the effective date of
the interim final FIP.
Comment: One commenter stated that
the EPA needs to control air quality
because hydraulic fracturing
(‘‘fracking’’) is under-regulated.
Response: The majority of oil and
natural gas wells drilled today are
hydraulically fractured. Hydraulic
fracturing occurs when wells are being
completed and recompleted. NSPS
OOOO ensures that VOC emissions are
controlled from the completion and
recompletion of natural gas wells.
Additionally, this FIP requires that
owners and operators of oil and natural
gas production facilities on the FBIR
reduce by at least 90% the VOC
emissions from casinghead natural gas
during the completion or recompletion
of any oil and natural gas well.
Together, these recent regulatory actions
will provide significant control of
emissions from hydraulic fracturing
activities.
Comment: Several commenters stated
that the EPA should set methane
standards in the final FIP noting that
methane is a greenhouse gas (GHG) with
a high carbon dioxide (CO2) equivalent,
and that leaked methane therefore
negatively influences climate change.
These same commenters also stated that
the EPA already requires control
technologies that could facilitate
emissions standards for methane and
that tribes have particular interest in
mitigating climate change because they
are disproportionately impacted by it.3
The commenters also stated that leaked
methane decreases a potentially
significant revenue stream for
producers. Another commenter stated
that flaring creates significant CO2
pollution, which contributes to climate
change.
Response: We had a very specific
purpose for developing this FIP, which
was to regulate VOC emissions from oil
and natural gas production operations
on the FBIR which represented the
largest source of air quality concerns at
this time. While this rule does not
directly regulate other pollutants subject
to regulation under the CAA, such as
the GHGs methane and CO2, it does
result in significant reductions of GHGs
because of the substantial methane
3 Commenter cites ‘‘EPA Tribal Science Council,
Tribal Science Priority’’ at 1 (June 2011). A copy of
the document is included in the docket for this rule,
Docket ID: EPA–R08–OAR–2012–0479, which can
be accessed at: https://www.regulations.gov.
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reduction as a co-benefit of the required
VOC control.
Comment: Other commenters
expressed concern about the dust now
prevalent in the area. The commenters
stated that excessive dust was often seen
in the air as well as on trees and grass.
Some commenters insisted that oil and
trucking companies should participate
in control of dust in the area. One
commenter stated that visible emissions
have not been responded to by the EPA
or the Three Affiliated Tribes of the
Mandan, Hidatsa, and Arikara Nation.
Response: This FIP is focused on
emissions of VOCs, and regulating
fugitive dust resulting from oil and
natural gas production activities on the
FBIR was not within the scope of the
rulemaking. If the EPA determines it is
necessary to regulate other pollutants,
we will address those at that time.
Generally, dust from road traffic is a
local issue and the public should
contact the local environmental or
health agency with these concerns. The
public can report possible harmful
environmental activity on the EPA’s
Web site at https://www.epa.gov/tips/.
Comment: Several commenters noted
a significant increase in truck traffic
since oil and natural gas production on
the FBIR had begun. One commenter
noted that the incidence of traffic
accidents, often fatal, has significantly
increased on the FBIR since production
has begun.
Response: Traffic in North Dakota and
on the FBIR is regulated by the Three
Affiliated Tribes of the Mandan,
Hidatsa, and Arikara Nation or the
United States Department of
Transportation, and not by the EPA and
thus is not within the EPA’s authority
to address.
Comment: One commenter discussed
being bothered by noticeable diesel
emissions from the increased truck
traffic. Another commenter noted that
an oil rig was polluting in close
proximity to a school.
Response: This FIP does not regulate
the exhaust emissions from the trucks or
oil rigs. These sources of emissions meet
the definition of on-road and non-road
motor vehicles (mobile sources) under
the CAA and are subject to regulations
under those provisions. This FIP only
regulates stationary oil and natural gas
production sources. A stationary source
is defined in the CAA (42 U.S.C.
7602(z)) to mean ‘‘generally any source
of an air pollutant.’’ The definition
specifically excludes those emissions
resulting directly from an internal
combustion engine for transportation
purposes or from a nonroad engine or
nonroad vehicle as defined in 42 U.S.C.
7550. This rule however does not
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exempt the owners and operators from
any other requirements under the CAA
to minimize pollutants and control
emissions from these sources.
Comment: Some commenters stated
that oil and natural gas development
had also negatively impacted water
quality. One commenter stated that the
water at her house is undrinkable and
is often too poor to be used for other
common functions like laundry. Some
commenters stated that they had
witnessed trucks dumping waste from
oil and natural gas production in
unauthorized locations, including the
ground near Skunk Bay.
Response: We acknowledge the
concerns expressed by the commenters
in regard to the effect that oil and
natural gas production activities may
have on water quality. Our authority to
issue this rule, however, falls under the
CAA. Water pollution on the FBIR is
addressed through separate regulations
established under the Clean Water Act
(CWA). Additional information about
the CWA can be found at https://
www.epa.gov/regulations/laws/
cwa.html. In addition, the public can
report possible harmful environmental
activity on the EPA’s Web site at https://
www.epa.gov/tips/.
Comment: One commenter
recommended that the EPA explore
voluntary partnerships with FBIR
producers in order to deploy best
practices for gas capture and use.
Commenter stated that this may allow
FBIR producers to demonstrate the
feasibility and benefits of
comprehensive gas capture at coproducing sites, and in doing so
encourage these practices for other
producers in the Bakken and elsewhere.
Response: We appreciate the
commenter’s suggestion; however, such
a partnership is outside of the scope of
this FIP and 40 CFR part 49. The
comment is more appropriately
addressed through the EPA’s voluntary
programs, such as the Natural GasSTAR
Program.4 Therefore we have forwarded
this comment on to the Natural
GasSTAR Program for their
consideration.
B. Legal Basis and Authority
Comment: Some commenters
disagreed with our assertion that the
rule is needed and justified to mitigate
hazards to the public health and the
environment, stating that actual
emissions are much lower than
potential emissions, and are low enough
to present no hazard to public health or
4 Information on the EPA’s Natural Gas STAR
Program is available online at: https://www.epa.gov/
gasstar/, Accessed November 15, 2012.
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the environment. The commenters
further stated that rather than the
protection of the public health and
environment, the purpose of this FIP is
to solve the ‘‘legal and hypothetical
problem’’ of ensuring potential
emissions do not exceed regulatory
applicability thresholds, such as the
PSD thresholds. The commenters stated
that the EPA proposed the FIP not to
improve already good air quality5 or to
satisfy CAA requirements, but because
many FBIR operators need
preconstruction permits and the EPA
lacks adequate time or resources to issue
those permits by the time the Consent
Agreement and Final Orders (CAFOs) 6
governing the sources expire.
Several commenters support the
proposed FIP and also agree that we
have just cause to mitigate hazards to
the public health and the environment
and with our assertion and that we are
acting in accordance with our trust
responsibilities to protect the public
health and environment in Indian
country.
Response: The purpose of this FIP is
to address potential impacts to the
public health and the environment. It
also solves some of the unusual
challenges that owners and operators on
the FBIR face with regard to compliance
with the permitting requirements of the
CAA. However, our primary purpose for
developing rules to regulate air
emissions is to meet the requirements of
the CAA to protect the public health
and the environment by providing those
living on the Reservation the same level
of air quality and health protection as
people living outside the Reservation.
So, while this FIP solves some of the
challenges that the owners and
operators on the FBIR face with regard
to requirements of the CAA, or more
specifically the PSD permitting
requirements, the primary focus is to
prevent the potential degradation of the
air quality on the FBIR.
The CAA is a comprehensive federal
law that regulates air emissions from
stationary and mobile sources. Among
other things, this law authorizes us to
establish National Ambient Air Quality
Standards (NAAQS) to protect public
health and the environment.
Amendments to the CAA codified the
PSD preconstruction permitting
program to protect the public health and
the environment from any actual or
potential adverse effects which may
reasonably be anticipated to occur
5 Commenter references the interim final rule at
77 FR 48886.
6 The FBIR CAFOs are included in the docket for
this rule, Docket ID: EPA–R08–OAR–2012–0479,
which can be accessed at: https://
www.regulations.gov.
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17839
notwithstanding attainment and
maintenance of the NAAQS.
Because of the high quantity of VOC
emissions present in the oil and natural
gas operations in the Bakken formation,
the absence of infrastructure to capture
excess volatile liquids, and the
regulatory gap that rendered the use of
control technology unenforceable prior
to the FIP, some sources had potential
emissions that would have required
major source permits. These
preconstruction PSD permits are one
mechanism available to the EPA to
assure that emissions increases
associated with economic development
do not threaten the NAAQS. Under the
Federal Tribal NSR rule, sources located
on the FBIR may also obtain synthetic
minor NSR permits to limit their
emissions below major source levels.
Either of these options would require
that the EPA review and issue several
hundred air permits to emissions
limitations similar to those required by
this FIP. We determined, therefore, that
issuing this FIP, and imposing emission
limitations for these sources at one time
was a more efficient and streamlined
mechanism than issuing individual
permits. We believe that this is the best
way to address the potential harm that
these previously unregulated VOC
emissions would create, and ensure that
we are not inhibiting the growth of oil
and natural gas due to the permitting
process, which could put the Tribe at an
economic disadvantage.
Finally, while actual emissions for
some sources may be lower than
potential emissions, there are no
federally and practicably enforceable
emission control requirements for the
affected equipment limiting the
potential to emit. This rule imposes
emission limitations that are federally
and practicably enforceable.
Comment: Several commenters stated
that by proposing to adopt this FIP, the
EPA is stepping into the shoes of the
Tribes and acting as the local air
pollution control authority. The FIP
includes a comprehensive set of control
measures for oil and natural gas
operations—imposing requirements on
such operations merely because they
exist and not because they have engaged
in an activity that triggers a regulatory
requirement, such as building a new
source or modifying an existing source
such that a PSD permit or a synthetic
minor NSR permit is needed. In other
words, the EPA is adopting what would
otherwise amount to a State
Implementation Plan (SIP) or TIP for the
FBIR. The authority for such a control
program necessarily flows from section
110(a), which specifies the measures
that a SIP may include. This section of
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the CAA specifies that a SIP may
‘‘include enforceable emission
limitations and other control measures,
means, or techniques * * * as may be
necessary or appropriate to meet the
applicable requirements of this
chapter.’’ CAA section 110(a)(2)(A)
(emphasis added). Thus, the EPA may
adopt as part of this FIP only those
measures that are needed to attain or
maintain NAAQS or to meet other
specified CAA applicable requirements.
Response: We disagree; the
commenter is mistaken that the
underlying authority for this FIP is
found in Section 110(a) of the Act.
Section 301(d) of the CAA, 42 U.S.C.
7601(d), directs us to promulgate
regulations specifying the provisions of
the Act for which it is appropriate to
treat Indian tribes in the same manner
as states. Pursuant to this statutory
directive, the EPA promulgated
regulations entitled, ‘‘Indian Tribes: Air
Quality Planning and Management’’
(TAR) (63 FR 7254, February 12, 1998).
Our regulations delineate the CAA
provisions for which it is appropriate to
treat tribes in the same manner as a
state. See 40 CFR 49.3, 49.4. Among
those provisions for which we
determined such treatment was
inappropriate are CAA section 110(a)(1)
(SIP submittal and implementation
deadlines) and CAA section 110(c)(1)
(directing the EPA to promulgate a
Federal Implementation Plan (FIP)
‘‘within 2 years’’ after we find that a
state has failed to submit a required
plan, or has submitted an incomplete
plan, or within 2 years after we
disapproved all or a portion of a plan).
See 40 CFR 49.4(a), (d); 63 FR 7262–
7266, February 12, 1998.
The TAR preamble clarified that by
including CAA section 110(c)(1) on the
§ 49.4 list, ‘‘EPA is not relieved of its
general obligation under the CAA to
ensure the protection of air quality
throughout the nation, including
throughout Indian country. In the
absence of an express statutory
requirement, EPA may act to protect air
quality pursuant to its ‘‘gap-filling’’
authority under the Act as a whole. See,
e.g. CAA section 301(a).’’ (63 FR 7265,
February 12, 1998). The preamble
confirmed that ‘‘EPA will continue to be
subject to the basic requirement to issue
a FIP for affected tribal areas within
some reasonable time.’’ Id. (referencing
§ 49.11(a) which provides that the
Agency will promulgate a FIP to protect
tribal air quality within a reasonable
time if tribal efforts do not result in
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adoption and approval of tribal plans or
program).7
The preamble to the TAR set forth our
view articulated in the proposed rule
that, based on the ‘‘general purpose and
scope of the CAA, the requirements of
which apply nationally, and on the
specific language of Sections 301(a) and
301(d)(4), Congress intended to give to
the Agency broad authority to protect
tribal air resources.’’ Id. at 63 FR 7262.
It further discussed our intent to ‘‘use its
authority under the CAA ‘to protect air
quality throughout Indian country’ by
directly implementing the Act’s
requirements in instances where tribes
choose not to develop a program, fail to
adopt an adequate program or fail to
adequately implement an air program.’’
Id.
The NDDoH, the CAA permitting
authority for areas of North Dakota
outside of Indian country, including
outside of the FBIR, has promulgated
rules to control emissions from oil and
natural gas production facilities. Since
there is not currently an approved TIP
specifically covering the reduction of
VOC emissions related to natural gas
emissions from oil and natural gas
production facilities on the FBIR, a lack
of regulation exists with regard to such
facilities operating within the exterior
boundaries of the Reservation. This FIP
establishes legally and practicably
enforceable requirements to control and
reduce VOC emissions. Therefore, in
this rule, we determined that it is
necessary and appropriate to exercise
our discretionary authority under
sections 301(a) and 301(d)(4) of the CAA
and 40 CFR 49.11(a) to promulgate a FIP
to remedy an existing regulatory gap
under the Act with respect to oil and
natural gas operations on the FBIR.
Comment: One commenter was
concerned that the Tribe would have
enforcement authority and be allowed to
act arbitrarily and capriciously with
regard to shutting down operations and
requested that the requirements of this
rule be enforced by the federal
government. The commenter stated that
the Three Affiliated Tribes of the
Mandan, Hidatsa, and Arikara Nation
should not be allowed to enforce the
rule because its elected officials have
economic interest in the oil and natural
gas industry, making them conflicted.
7 Section 49.11(a) states that the Agency, ‘‘[s]hall
promulgate without unreasonable delay such
federal implementation plan provisions as are
necessary or appropriate to protect air quality,
consistent with the provisions of sections 301(a)
and 301(d)(4), if a tribe does not submit a tribal
implementation plan meeting the completeness
criteria of 40 CFR part 51, Appendix V, or does not
receive EPA approval of a submitted tribal
implementation plan.’’ 40 CFR 49.11(a).
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Response: At this time, EPA has not
delegated to the Three Affiliated Tribes
of the Mandan, Hidatsa, and Arikara
Nation the authority under these
regulatory provisions to enforce the
provisions of this FIP. The provisions in
§ 49.4162 of the Code of Federal
Regulations establish the steps by which
the Three Affiliated Tribes of the
Mandan, Hidatsa, and Arikara Nation
may request delegation to assist us with
the administration of this rule. As
described in the regulatory provisions
and the preamble to the proposed rule,
any such delegation will be
accomplished through a delegation of
authority agreement between the EPA
Region 8 Administrator and the Three
Affiliated Tribes of the Mandan,
Hidatsa, and Arikara Nation. In the
event such an agreement is reached, the
rule would continue to operate under
federal authority throughout the FBIR,
and the Three Affiliated Tribes of the
Mandan, Hidatsa, and Arikara Nation
would assist us with administration of
the rule to the extent specified in the
delegation agreement.
C. Rule Development and
Implementation
Comment: One commenter indicated
that the State of North Dakota was
issuing permits to drill on the FBIR and
asserted that the State has been giving
out drilling permits ‘‘like candy,’’
leading to an overwhelming level of oil
and natural gas development and
increase in pollution on the FBIR. The
commenter stated that the Tribe did not
have, nor did they develop, necessary
regulations when development began,
and that the Tribe, as well as the EPA,
is now playing ‘‘catch-up.’’
Response: We acknowledge the
commenter’s concern with increased oil
and natural gas development on the
FBIR, as well as increased development
under the State of North Dakota’s
jurisdiction and the need for
reservation-specific regulations to
protect public health and the
environment. We note that the State of
North Dakota does not have jurisdiction
over development on the FBIR. As
discussed in the preamble for the
interim final rule, we first became aware
of the need to address VOC emissions
from these operations in August of 2011.
At that time, a significant number of
entities engaged in oil and natural gas
operations on the FBIR informed us that
the emissions of regulated air
pollutants, including VOC, were
significantly larger than previously
understood and larger than emissions in
other areas, due to the geologic
characteristics and infrastructure
challenges in the Bakken formation. At
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that time, we immediately took
measures to ensure that VOC emissions
were appropriately controlled by
entering into CAFOs with the owners/
operators to implement VOC controls.
We then developed and promulgated
this FIP as an interim final rule to
immediately establish federally and
practicably enforceable emission control
requirements for the affected
equipment. In addition, given the
number of existing facilities that were
operating as unregulated sources, we
determined that existing facilities
should also be subject to the FIP. We
believe the series of actions taken to
address the unregulated sources of VOC
emissions on the FBIR occurred as soon
as practicable after becoming aware of
the issue.
Comment: One commenter stated that
the EPA had accelerated development of
this FIP without consideration of its
impact on the community to avoid
disrupting the pace of oil and natural
gas development. Another commenter
stated that this FIP is not strict enough,
citing the estimated potential long-term
development of 1,000 oil and natural
gas facilities by 2029 as discussed in the
interim final rule (77 FR 48887).
Response: We disagree with the
assertion that the expedited process for
developing this FIP did not take into
consideration the impacts of oil and
natural gas development on the
community. The mitigation of the air
quality impact of oil and natural gas
development on the FBIR was a priority
when developing this rule. This rule
will reduce VOC emissions from
existing operations and limit the
amount of VOC emissions from
potential new development. Our intent
is to level the health protections
between the residents living on the FBIR
and the residents living in the State of
North Dakota. In other words, the EPA
intends that the FBIR residents receive
equivalent air quality protections as
those residing in the State. We acted
quickly in developing this FIP in order
to provide those protections as soon as
possible and avoid unnecessary
disruption to oil and natural gas
development. While the FIP
development process has been quick, as
discussed in this notice we have
provided for full public participation
and fully responded to all concerns.
We also disagree that the FIP is not
strict enough. This FIP establishes
requirements to control air pollution in
the form of VOC emissions from oil and
natural gas production and storage
operations on the FBIR, comparable to
those requirements developed by state
permitting authorities. In addition, this
FIP imposes emission reduction
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requirements that are robust and
consistent with the control technology
requirements for the oil and natural gas
production and storage industry under
NSPS OOOO.
Comment: One commenter stated that
an environmental impact statement
(EIS) was not required prior to leasing
the tribal land for oil and natural gas
development. The commenter noted
that a programmatic environmental
assessment (EA) is being conducted, but
insisted that the more rigorous EIS
should have been required. The
commenter questioned whether it was
legal for the EIS requirement to be
bypassed, and stated that the
requirements of the National
Environmental Policy Act (NEPA) had
been ‘‘minimized.’’ Therefore, the
commenter asserted that area residents
were denied the opportunity to make
statements regarding the impact of oil
and natural gas development on their
lives. Another commenter stated that
the lack of adequate public notice for
the EA was not compliant with NEPA
and environmental justice.
Response: This FIP only regulates the
VOC air pollutant emissions generated
by the well completion and production
and storage operations on the FBIR and
is not subject to the requirements of
NEPA (EIS or EA). A FIP is an action
under the CAA and Section 7(c) of the
Energy Supply and Environmental
Coordination Act of 1974 (15 U.S.C.
793(c)(1)) exempts actions under the
CAA from the requirements of NEPA,
specifically this section reads ‘‘* * * (c)
Major federal actions significantly
affecting the quality of the human
environment (1) No action taken under
the Clean Air Act [42 U.S.C. 7401 et
seq.] shall be deemed a major Federal
action significantly affecting the quality
of the human environment within the
meaning of the National Environmental
Policy Act of 1969 [42 U.S.C. 4321 et
seq.].’’ Therefore a NEPA analysis is not
required for this FIP.
Leasing of the mineral rights and
drilling of the oil and natural gas wells
is regulated by the Bureau of Indian
Affairs (BIA) and the Bureau of Land
Management (BLM). Those federal
agencies are undertaking any applicable
NEPA requirements when approving
leasing and drilling activities.
Comment: Many commenters asserted
that this FIP falls short of its stated
purpose because some facilities’
potential to emit (PTE) of VOCs or any
other regulated NSR pollutant may
exceed the applicability thresholds for
PSD permitting resulting in the need for
a synthetic minor NSR permit issued
under Federal Tribal NSR Rule (if PSD
permitting is to be avoided) even after
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17841
applying the legally and practicably
enforceable emission reductions
provided in this rule (77 FR 48885).
Several commenters stated that the EPA
should declare in the final FIP that all
sources that become minor under the
Federal Tribal NSR rule will be
considered ‘‘true minor’’ sources. More
specifically, commenters claim that
sources treated as synthetic minor
sources under this FIP could not install
new wells for the foreseeable future
because the EPA has not developed an
expeditious process for issuing
synthetic minor NSR permits.
Another commenter questioned why
owners and operators working within
the FBIR would be allowed to exceed
VOC emission standards.8 The
commenter asked if there was any point
in setting these standards if permits
could be obtained to exceed them.
Response: The owners and operators
subject to this FIP are not allowed to
exceed established standards, and
nothing in this FIP is intended to relieve
the owners and operators of the
responsibility to comply with all federal
environmental laws and rules. This rule
does not replace any requirement to
obtain permission to construct under
the PSD regulations at 40 CFR 52.21 or
the Federal Tribal NSR regulations at 40
CFR 49.151; therefore, this FIP does not
automatically create ‘‘true minor’’ status
for those sources that become minor
under the Federal Tribal NSR Rule.
Owners and operators complying with
this rule may still be required to obtain
preconstruction permits to further
reduce VOC emissions or the emissions
of other pollutants that are regulated by
the PSD and Federal Tribal NSR
permitting regulations if the emissions
thresholds for these regulations are
exceeded. Further, this rule does not
automatically make sources synthetic
minor sources for purposes of the PSD
regulations. A synthetic minor source is
generally understood to include any
source that would be major but for a
requested enforceable limitation. For
example, a source can become a
synthetic minor source when the owner
or operator requests a synthetic minor
NSR permit through the Federal Tribal
NSR regulations to avoid major source
requirements of PSD and that request is
approved and the permit is issued.
This rule is similar to NSPS OOOO
promulgated at 40 CFR part 60,
NESHAP HH promulgated at 40 CFR
part 63, and the NDDoH regulations
specific to oil and natural gas
production operations at Chapters 33–
8 The commenter is referring to the interim final
rule Section III.E. ‘‘Effect on Permitting of
Facilities.’’ (77 FR 48885).
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15–07 and 33–15–20 of the North
Dakota Administrative Code, none of
which replace CAA permitting
requirements. Similar to the NSPS,
NESHAPs, and NDDoH regulations, this
rule provides legally and practicably
enforceable restrictions for VOC
emissions on an emission unit specific
basis. Any reductions realized by
complying with this rule can then be
used to calculate the PTE of VOCs when
determining whether any CAA
permitting may be required. In addition,
the rule only requires controls on VOC
emissions, because of the high amount
of associated natural gas in the crude oil
from the FBIR and the absence of
infrastructure to capture the natural gas
emissions. Therefore, any potential
emissions of VOCs or any other criteria
pollutant that exceed the PSD
permitting thresholds after taking credit
for the enforceable restrictions in this
rule would still result in the
requirement to obtain a PSD permit for
permission to construct. A synthetic
minor NSR permit to avoid the PSD
permitting requirements can still be
requested through the Federal Tribal
NSR regulations. Those facilities with
potential emissions of VOCs and all
other criteria pollutants that are below
the PSD permitting thresholds and
above the Federal Tribal NSR permitting
thresholds after complying with the
requirements of this FIP would be
considered true minor sources under the
Federal Tribal NSR regulations.
Finally, regarding the commenter’s
claim that sources treated as synthetic
minor sources under this FIP could not
install new wells for the foreseeable
future because the EPA has not
developed an expeditious process for
issuing synthetic minor permits, the
EPA has issued and continues to issue
synthetic minor permits to sources on
the FBIR to those who request them.
Comment: Several commenters
requested that the EPA clarify that a
stationary source and corresponding
minor NSR permitting requirements
apply to operations and equipment on a
well pad and immediately appurtenant
operations. These commenters also
urged the EPA to clarify that
geographically separated ‘‘well pads and
related operations’’ should not be
aggregated into one stationary source
simply because they are connected by
gathering or production lines. The
commenters asserted that the EPA’s use
of the term ‘‘integrally connected’’ (77
FR 48885) could create confusion as to
what equipment and activities are
considered part of a facility. The
commenters cited Summit Petroleum
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Corp. v. EPA 9 as an example of the EPA
incorrectly aggregating multiple wells,
well pads and related facilities that were
geographically widespread into one
single facility for the purposes of the
CAA. The commenters stated that such
an approach is ‘‘nonsensical’’ and
inconsistent with the CAA definition of
‘‘stationary source.’’ The commenters
also requested that the EPA explain the
limited circumstances in which
aggregation into a ‘‘facility’’ or
‘‘stationary source’’ is appropriate, and
suggested the following as those
circumstances; When: (1) The
operations share a single two-digit major
SIC code; (2) the operations are under
common ownership or control; and (3)
the operations are physically contiguous
or physically proximate. The EPA
should specify that functional
interrelatedness should not be used to
determine physical proximity.
Response: This action affects facilities
operating on the FBIR in North Dakota,
and thus the 6th Circuit’s Summit
Petroleum decision cited by the
commenters does not apply.10 When the
EPA issues permits to sources that are
also subject to this rule, the ultimate
determination regarding the scope of the
stationary source to be permitted will be
made by implementing the stationary
source definition contained in the
federal NSR and Title V regulations (40
CFR 52.21(b)(5) and (6), 71.2). Such
determinations are highly fact specific
and will continue to be made on a caseby-case basis, applying the relevant
regulatory criteria to the facts of the oil
and natural gas production activities
being permitted.
Comment: Several commenters stated
that the final FIP should refer to Bakken
Pool wells located on the FBIR simply
as ‘‘oil wells’’ or ‘‘Fort Berthold Indian
Reservation wells’’ rather than using the
phrases ‘‘oil and natural gas production
wells’’ or ‘‘oil and natural gas
production facilities.’’ The commenters
asserted that using the characterization
‘‘oil wells’’ is consistent with related
EPA rules.11 One commenter also stated
9 Summit Petroleum Corp. v. EPA, Nos. 0904348,
10–4572 (Sixth Cir. 2012) at 1. The document is
included in the docket for this rule, Docket ID:
EPA–R08–OAR–2012–0479, which can be accessed
at: https://www.regulations.gov.
10 Memo from Stephen D. Page, Director, Office of
Air Quality Planning and Standards, to Regional Air
Division Directors, Regions 1–10, Applicability of
the Summit Decision to EPA Title V and NSR
Source Determinations (Dec. 21, 2012), available at
https://epa.gov/nsr/documents/SummitDecision.pdf
and included in the docket for this rule, Docket ID:
EPA–R08–OAR–2012–0479, which can be accessed
at: https://www.regulations.gov.
11 Commenter specifically mentions the ‘‘New
Source Performance Standards for Crude Oil and
Natural Gas Production, Transmission and
Distribution’’ (40 CFR part 60, subpart OOOO) and
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that North Dakota permits refer to these
as oil wells. On the other hand, two
commenters stated that they support the
inclusion of co-producing oil and
natural gas wells, which are defined as
‘‘oil and natural gas production
facilities’’ in this FIP.
Response: The reference to the
Bakken Pool 12 production facilities as
oil and natural gas production facilities
in this FIP is consistent with: (1)
NDDoH regulations at 33–15–20 which
defines an oil well as ‘‘any well capable
of producing oil or oil and casinghead
gas from a common source of supply’’;
and (2) the NDDoH’s Bakken Pool
Guidance 13 (Bakken Pool Guidance)
which refers to the facilities as oil and
gas production facilities, both of which
form the basis of this rule. We believe
this reference adequately describes the
affected facilities under the FIP and is
consistent with NDDoH regulations and
guidance.
We acknowledge the commenter’s
assertions that the facilities may be
described differently in other EPA
regulations. Although the Bakken Pool
production wells on the FBIR would be
considered oil wells based on the
discussions in NSPS OOOO and
Subpart W (76 FR 80567), those
discussions do not adequately reflect
the volume of natural gas coproduced
from a Bakken Pool well. NSPS OOOO
and Subpart W are national rules, and
therefore, the discussions they contain
must be broad enough to apply
nationwide. Since this a reservationspecific FIP, we believe it is appropriate
to use a more focused definition, as did
the State of North Dakota in the Bakken
Pool Guidance, due to the unique nature
of the oil being produced from the
Bakken Pool.
D. Applicability
Comment: Several commenters stated
that the FIP should establish a
minimum emissions threshold for
applicability, which exists in NSPS
OOOO.
Response: The only minimum
emission threshold for applicability that
the ‘‘Greenhouse Gas Reporting Rule’’ (40 CFR part
98, subpart W).
12 The Bakken Pool is defined as a compilation of
crude oil formations consisting of Bakken, Sanish
and Three Forks formations.
13 Bakken Pool Oil and Gas Production Facilities
Air Pollution Control Permitting & Compliance
Guidance, NDDoH Air Quality Division, May 2,
2011. This guidance document was developed by
the Bakken VOC Task Force. The Bakken VOC Task
Force was a collaboration between the NDDoH and
the owners and operators of oil and gas operations
producing from the Bakken Pool. A copy of the
guidance document is included in the docket for
this rule, Docket ID: EPA–R08–OAR–2012–0479,
which can be accessed at: https://
www.regulations.gov.
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exists in NSPS OOOO and could apply
to emission units regulated under this
FIP is the 6 tpy applicability threshold
for storage tanks. While this FIP does
not provide the same applicability
threshold for tanks as that found in
NSPS OOOO, it does exempt storage
tanks that are or become subject to the
requirements of NSPS OOOO. See
§ 49.4164(f). However, several tanks
operating on the FBIR prior to the
applicability date of NSPS OOOO are
not subject to NSPS OOOO. Therefore,
since these tanks are not subject to
NSPS OOOO and do not have a
minimum emissions threshold for
applicability, we decided that it was
appropriate to regulate these tanks in a
manner consistent with NDDoH
requirements for tanks at oil and natural
gas production facilities outside the
FBIR. Specifically, the Bakken Pool
Guidance at Appendix D and this FIP at
§ 49.4164(d)(2)(ii), allow for a reduced
VOC destruction efficiency and the use
of pit flares where the PTE of VOCs
from the aggregate of all produced oil
storage tanks and produced water
storage tanks interconnected with
produced oil storage tanks at an oil and
natural gas production facility is less
than, and reasonably expected to remain
below, 20 tons in any consecutive 12month period. The commenters failed to
provide any supporting information on
appropriate applicability thresholds for
the other production equipment
regulated under this FIP. As previously
discussed, we believe the volume of
VOC emissions from oil and natural gas
operations on the FBIR warrants
specially tailored regulation, which we
have developed in this FIP, and which
NDDoH developed in their Bakken Pool
Guidance. At this time, we do not have
sufficient information to establish
minimum thresholds for other
production equipment.
Comment: Several commenters stated
that the EPA should clarify that the FIP
statements ‘‘[t]he completion date is
considered the date that construction at
an oil and natural gas production
facility has commenced’’ (77 FR 48885),
and ‘‘[t]he recompletion date is
considered the date that a modification
has occurred at an oil and natural gas
production facility’’ (77 FR 48885) are
for the purposes of determining whether
this FIP applies to a particular oil
production facility and does not apply
to other EPA rules or programs.
Response: We agree that the suggested
clarification is necessary. We have
added language to the applicable
provision (§ 49.4161(b)) to indicate that
the correlation of the initiation of well
completion operations and well
recompletion operations to the dates
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that construction and modifications
commence is specific to this rule. In
addition, we have changed the language
to clarify that the compliance date is
upon initiation of well completion
operations and well recompletion
operations.
Comment: Several commenters
disagree with the EPA’s assertion
contained in the NSPS OOOO that
recompletion of an existing well
constitutes a modification. Because the
EPA acts in accordance with the NSPS
OOOO regarding this position, the
commenters restated the position they
had voiced in comments on the
proposed NSPS OOOO. The
commenters concluded that this same
error should not be perpetuated in the
final FIP.
Response: The issue of what
constitutes modifications under CAA
section 111 was decided by EPA in the
prior rulemaking and is not being
reopened here. While we are not
statutorily compelled to use the same
definition here, we think it is
appropriate to do so and commenters
have not provided a policy basis on
which to revisit EPA’s conclusion. As
explained in detail in section IX.A. of
the preamble for the final Federal
Register notice of NSPS OOOO (77 FR
49510), a completion operation
associated with refracturing is
considered a modification under CAA
section 111(a) because a physical
change occurs to the well resulting in
emissions increases during the
recompletion operation. When
determining applicability for the rule,
we used August 12, 2007, which is the
earliest well completion date identified
in the CAFOs and thus the earliest well
completion date information available
to the EPA at the time of the
rulemaking. Due to the nature of
operations producing from the Bakken
Pool and the significant amount of coproduced natural gas emissions, it is
important that modified facilities are
required to control emissions from
affected equipment. We believe
including the definition of a modified
facility in the final FIP is important
because it will require the control of
emissions from the recompletion of any
existing well that was completed prior
to August 12, 2007 that the agency may
not have been aware of at the time of the
rulemaking and that would not be
subject to the rule prior to a
modification.
Comment: One commenter urged the
EPA to include pollution control
requirements for dehydration units,
pneumatic controllers and pumps, and
compressors, stating that these sources
could be significant sources of
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17843
pollution. The commenter requested
that the EPA incorporate the
requirements for compressors and
pneumatics from the NSPS OOOO, at a
minimum.
Response: We agree with the
commenter that dehydration units,
pneumatic controllers and pumps, and
compressors are other sources of air
pollution that may be operating at the
oil and natural gas production facilities
on the FBIR. We reviewed information
provided in 154 applications for
synthetic minor NSR permits submitted
to the Region 8 office 14 during the
development of the FIP. Based on these
applications, we were able to determine
that the most significant sources of the
VOC emissions are the pieces of
equipment used to produce the oil and
natural gas during well completions,
phase separation of the extracted
reservoir fluids (heater-treater), and the
temporary storage of the crude oil
(tanks). The information in the
applications indicates pneumatic
devices, dehydration units,
compressors, and associated fugitive
emissions listed in the applications
were minor sources of VOC emissions
when compared to other emission units.
Therefore, requirements for this
equipment have not been included in
this rule. If we determine at a later date
that there is a need for control of VOC
emissions from oil and natural gas
production equipment and operations
not covered by this rule, we may
propose additional FIPs or propose
supplements to this FIP.
Comment: Several commenters stated
that the EPA should remove all
requirements applicable to heater-treater
combustion devices from the FIP. The
commenters asserted that the use of
heater-treater combustion devices can
already be taken into account when
determining PTE because they are
‘‘inherent process equipment,’’ and that
additional requirements for these
devices are therefore unnecessary. The
commenters cited criteria from the EPA
letters 15 and the Compliance Assurance
Monitoring (CAM) rulemaking 16 to
14 The applications can be found in the docket for
this rule, Docket ID: EPA–R08–OAR–2012–0479,
which can be accessed at https://
www.regulations.gov.
15 Letter from EPA to Mr. Timothy J Mahin, Intel
Government Affairs, dated November 27, 1995; see
also Letter from EPA to Edward R. Herbert III,
Director of Environmental Affairs, National Ready
Mixed Concrete Association, July 10, 2002,
included in the docket for this rule under Docket
ID: EPA–R08–OAR–2012–0479, which can be
accessed at: https://www.regulations.gov.
16 ‘‘CAM Response to Comments, Part III,’’ at 6–
7, October 2, 1997, available online at https://
www.epa.gov/airtoxics/cam/ricam.html and
included in the docket for this rule under Docket
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argue that heater-treater combustion
devices must be considered inherent
process equipment based on those
criteria.
The commenters stated that the EPA’s
description of the heater-treater
combustion device requirement in the
FIP mandates the use of such devices at
oil facilities, primarily for safety and
product recovery, and does not address
air quality concerns (77 FR 48883–
48884).
The commenters also stated that the
possibility of some oil facilities
operating without heater-treater devices
is not an appropriate justification for the
FIP requirements, because any facilities
operating as such would be in clear
violation of standard operating
procedures which ensure safe working
conditions. The commenters insisted
that the EPA should not base this
justification on ‘‘unsupported
assumptions’’ that standing laws are
being violated or inadequately enforced.
Response: We acknowledge that the
preamble at 77 FR 48883 states that the
oil/natural gas/water emulsion from the
production wells is transported through
2-phase separators (separators), which
are an inherent component of the
pipeline. We also state in the same
paragraph that following the 2-phase
separator, the emulsion enters a 3-phase
separator (heater-treater), which is a
necessary step in the production process
and produces gas that is separated from
the emulsion. However, until the
separated gas from the heater-treater is
captured as product or used in some
other beneficial way at the facility (e.g.,
a fuel source for gas burning equipment)
it is a significant source of the high
volume VOC emissions we determined
requires control to protect public health
and the environment on the FBIR.
Throughout the rulemaking process, one
of our priorities was to equalize the
requirements that apply to sources
operating in the State of North Dakota’s
jurisdiction with the requirements that
apply to sources outside of the State’s
jurisdiction. The NDIC regulations
found in the Control of Oil and Gas
Resources at Chapter 38–08–06 require
that natural gas from the heater-treaters
be routed to a natural gas gathering
pipeline as soon as practicable. When a
pipeline is not available, the natural gas
produced in the heater-treater process is
required to be routed to a control system
or device. While we acknowledged in
the preamble for the interim final rule
that the purpose of the NDIC
requirements was principally for safety
and product recovery reasons, we also
ID: EPA–R08–OAR–2012–0479, which can be
accessed at: https://www.regulations.gov.
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acknowledged that the requirements for
heater-treaters were modeled after the
Bakken Pool Guidance which requires
that the emissions from heater-treaters
be controlled.
E. Control Equipment and Requirements
Comment: One commenter stated that
flares of roughly 40 feet are a usual sight
in Mandaree and can be a nuisance to
area residents because of light and noise
pollution. Another commenter stated
that flares were not being lit when they
should have.
Response: We acknowledge the
concerns expressed by the commenters
and offer a clarified explanation of the
purpose and operation of the flares
being used by operators of oil and
natural gas production facilities on the
FBIR.
The purpose of flaring the natural gas
that is coproduced when extracting oil
from the FBIR wells is to prevent the
emission of VOC gases that might
otherwise be vented to the ambient air
when the natural gas cannot be captured
and injected into a sales pipeline. The
flames from the flares indicate that the
VOCs are actually being combusted. The
flares should be lit at all times that coproduced natural gas is being routed to
them rather than to the sales pipeline.
In situations where production facilities
are able to take advantage of existing
infrastructure and inject produced gas
into a pipeline, flaring is significantly
reduced, in some cases to the point of
only occurring as a backup control
measure in the event that pipeline
injections of all or part of the produced
natural gas becomes temporarily
infeasible. Situations at production
facilities that are unable to route the gas
to a sales pipeline and where flares are
not visibly operating may indicate the
flares are not being operated properly
and gas is being vented directly to the
ambient air. This FIP has appropriate
monitoring, recordkeeping, and
reporting requirements to ensure that
the flares are operating properly.
Further, because the FIP intends to limit
the use of flares in favor of capture and
injection of the produced natural gas
into sales pipelines as soon as
practicable, secondary impacts such as
noise and light pollution from
combustion of gas are expected to be
reduced by the owner or operator
complying with the rule.
Comment: One commenter speculated
that the level of emissions from flares is
above the allotted amount.
Response: It is unclear what is meant
by the term ‘‘allotted amount.’’ The
majority of oil and natural gas
production facilities currently in
operation on the FBIR do not hold any
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air pollution control permits that
specify any ‘‘allotted amount’’ of
emissions from the flares. Should the
combustion emissions from flaring
exceed the major source permitting
thresholds under PSD specified at 40
CFR 52.21, the owner or operator would
be required to obtain a PSD permit or
may opt to obtain a minor NSR permit
to become synthetically minor for
purposes of PSD prior to beginning
actual construction, independently of
this FIP. Either of these permits would
require the installation of control
technology sufficient to ensure
protection of air quality.
Comment: Several commenters stated
that the EPA should eliminate the 500
hour limitation on pit flare usage
because it is inconsistent with the
Bakken Pool Guidance and unnecessary.
One commenter wondered why use of
the pit flare was limited to 500 hours
per year and not something different.
The commenters also asserted that only
being allowed to assume 90% VOC
destruction and removal efficiency
(DRE) for pit flares already limits the
amount of pit flaring that could occur
without exceeding major source
thresholds. The commenters also stated
that a limitation on the use of pit flares
punishes operators that inject recovered
produced natural gas and natural gas
emissions into existing pipeline
infrastructure to sell it, because 98%
VOC DRE control devices are more
costly. Another commenter asked who
will monitor the pit flare operations and
what the repercussions are if a source
exceeds the limit of 500 hours of
operation in any consecutive 12-month
period?
Response: We disagree with the
commenters that the 500 hour limitation
on pit flare usage is unnecessary. The
purpose of the 500-hour per year limit
on use of a pit flare as a backup control
device in instances where injection of
produced natural gas and natural gas
emissions is temporarily infeasible is to
discourage the use of pit flares as a
primary control device. Based on past
EPA guidance 17 that addresses backup
situations, we have concluded that
applying a 500 hour per year limit to the
oil and natural gas production facilities
for the use of a pit flare in backup
situations is reasonable and consistent
with backup operation timeframes
17 Memo from John S. Seitz, Director, Office of Air
Quality Planning and Standards, to Regional Air
Division Directors, Regions 1–10, Calculating
Potential to Emit (PTE) for Emergency Generators
(September 6, 1995), available at https://epa.gov/
region07/air/title5/t5memos/emgen.pdf and
included in the docket for this rule under Docket
ID: EPA–R08–OAR–2012–0479, which can be
accessed at: https://www.regulations.gov.
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allowed for other industry sectors. In
addition, past EPA enforcement
settlements 18 19 that address backup
situations have led us to conclude that
500 hours (or 21 days) is a reasonable
period of time for owners and operators
of oil and natural gas production
facilities to address these situations and
maintain compliance with the rule.
During development of the draft
synthetic minor NSR permits prior to
this rule, we had discussions with
owners and operators indicating that
many oil and natural gas production
facilities on the FBIR regularly utilize
temporary 98% VOC DRE control
devices while they are preparing a
facility for permanent production and
storage operations;20 therefore, we
18 Consent Decree United States of America v.
Marathon Petroleum Company, LP, and
Catlettsburg Refining, LLC, available at: https://
epa.gov/compliance/resources/decrees/civil/caa/
marathonrefining-cd.pdf and included in the docket
for this rule under Docket ID: EPA–R08–OAR–
2012–0479, which can be accessed at: https://
www.regulations.gov.
19 Consent Decree United States of America, and
the State of Indiana, and Plaintiff Intervenors v. BP
Products North America, Inc, available at: https://
epa.gov/compliance/resources/decrees/civil/caa/
whiting-cd.pdf and included in the docket for this
rule under Docket ID: EPA–R08–OAR–2012–0479,
which can be accessed at: https://
www.regulations.gov.
20 As discussed in the preamble for the interim
final rule (77 FR 48880), the EPA Region 8 air
permit and enforcement programs hosted a Fort
Berthold Oil and Natural Gas Production Minor
NSR Permitting Process Meeting with the oil
producers in late August 2011. Representatives
from the Tribes were invited and attended in person
and by phone. Discussions included the anticipated
permitting timeline for permit applications
submitted by the oil producers. Between August 23
and September 1, 2011, a draft example synthetic
minor permit was sent by EPA to the meeting
attendees and the Tribes in preparation for the next
meeting on September 1, 2011. Then, on September
1, 2011, Region 8 hosted a permitting workshop.
Representatives from the various oil producers and
the Tribes were invited and attended.
Representatives of the NDDoH also participated by
phone. The minor NSR permitting process was
discussed, as well as questions that the companies
submitted ahead of time. The group began
discussions on the draft example permit and set up
a workshop specifically to delve into the specific
permit conditions for the following week. On
September 7 and 8, 2011, the EPA hosted a two-day
follow-up permitting workshop. All previous
meeting attendees were invited, including the
Tribes. Participants included the oil producers and
their consultants. NDDoH representatives were also
on the phone. At this meeting the group went
through the draft example permit and discussed the
proposed conditions and appropriate edits. Also
discussed was what would constitute a complete
application (administrative and technical) and the
various methods of PTE calculation proposed by the
companies in attendance. The EPA Region 8 hosted
an additional meeting on November 30, 2011 to
discuss the revised example permit, and
representatives from the various oil producers and
the Tribes were invited and attended. During these
permitting workshops, it was brought to our
attention that owners and operators routinely use
temporary, portable utility flares capable of
achieving a 98% VOC DRE for the initial period
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concluded it is reasonable to expect that
an owner or operator could acquire one
of these temporary control devices in
situations where use of the pipeline may
be infeasible for more than 500 hours.
The final rule requires the owners and
operators to monitor and keep records of
the hours that a pit flare is operated, a
description of the justification for use
and the volume of gas sent to it, to
ensure that the EPA can make a
determination, if necessary, that
injection of produced natural gas and
natural gas emissions into a pipeline for
sale or other beneficial purpose, or the
use of the primary control device, has
been maximized. Any deviations of
these requirements must be reported to
the EPA.
Comment: Several commenters stated
that the EPA should clarify that 98%
DRE utility flares and combustors are
not required to be installed as backup
control devices if an operator chooses to
route vapors to a production line and
use a 90% VOC DRE control device as
backup. The commenters stated that
such a clarification would prevent
operators tied into a sales line from
keeping utility flares or combustors idle
and on-site for infrequent backup use.
Response: We agree. While the rule
does not require the use of utility flares
and combustors as back-up control
devices if the owner or operator is
routing produced natural gas and
natural gas emissions to a sales line, the
rule does not clearly state this. The rule
has been clarified.
Comment: Commenters stated that
control requirements during
completions, recompletions, and for the
first 90 days of production are
insufficient. The commenters urged the
EPA to require that any flaring under
the FIP be performed using an enclosed
vent system, along with a utility flare or
a similar device, which is capable of
98% VOC DRE.
Response: We disagree with the
commenter that control requirements
during completions, recompletions, and
for the first 90 days of production are
insufficient. This FIP establishes
requirements to control air pollution in
the form of VOC emissions from oil and
natural gas production and storage
operations on the FBIR, comparable to
those requirements developed by state
permitting authorities. In other words,
we were motivated to level the playing
field for the regulated community. With
that in mind, the NDIC and NDDoH
when a new oil and natural gas production facility
is being prepared for permanent operations. A copy
of the attendee list for each meeting has been
included in the docket for this rule under Docket
ID: EPA–R08–OAR–2012–0479, which can be
accessed at: https://www.regulations.gov.
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17845
allow the use of pit flares or other 90%
VOC DRE control devices during
completions and recompletions. Shared
by both the State of North Dakota and
the EPA, another reason to limit the
required VOC destruction efficiency to
90% VOC DRE is that an owner or
operator may be put at a significant
economic disadvantage if they purchase
and install the much more expensive
98% VOC DRE control devices and
within the first 90 days after the first
date of production a well is found to be
too low producing to justify continued
production and must be shut-in.
Comment: Several commenters stated
that the EPA must clarify that emissions
from completion and recompletion
operations do not need to be vented to
a flare until the level of VOC is
sufficient to support combustion. The
commenters asserted that one might
interpret the FIP language which
required each owner or operator to
‘‘route all casinghead natural gas to a
utility flare or a pit flare capable of
reducing the mass content of VOC by at
least 90%’’(77 FR 48895) to include
venting materials that are not flammable
and therefore unable to sustain
combustion. The commenters stated that
such an interpretation would make
compliance with the rule impossible, as
vented materials are typically not
flammable in the early stages of
completion or recompletion. The
commenters cite ‘‘Letter to Mr. Matthew
Todd from Peter Tsirigotis, Director,
Sector Policies and Programs Division
(Sept. 28, 2012)’’ as evidence that the
EPA recently reached a similar
conclusion.21
Response: While the regulatory
language at § 49.4164(b) in the interim
final rule is not specific on this point,
the recordkeeping requirements for well
completion and recompletion
operations in § 49.4167(a)(4)(ii) of the
interim final rule specifically require
logging the date, time, and duration of
any venting of casinghead natural gas
from the oil and natural gas well; and
specific reasons for each instance of
venting in lieu of capture or
combustion. Therefore, this requirement
allows some degree of venting materials
that may not be flammable during well
completion and recompletion
operations.
Comment: Several commenters stated
that this FIP is inconsistent with NSPS
OOOO and adds further confusion for
operators who will be required to
comply with both sets of requirements.
21 A copy of the letter has been included in the
docket for this rule under Docket ID: EPA–R08–
OAR–2012–0479, which can be accessed at:
https://www.regulations.gov.
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Federal Register / Vol. 78, No. 56 / Friday, March 22, 2013 / Rules and Regulations
These commenters further state that for
all sources to which NSPS OOOO
applies, the FIP should mirror NSPS
OOOO requirements for oil and
produced water tank control devices.
Specifically, the commenters stated that
because the NSPS OOOO does not take
effect for tanks for one year, the
inconsistency results in an unnecessary
burden. The commenters also asserted
that since NSPS OOOO does not apply
to heater-treaters, the requirements in
the FIP for heater-treaters should mirror
the requirements of the NDDoH
regulations precisely. The commenter
also expressed concern that the terms of
NSPS OOOO are still subject to
challenges that have not been resolved,
although the commenter indicated that
the EPA was in discussions with
industry representatives to resolve those
issues.
Response: We disagree that
differences between this FIP and NSPS
OOOO result in an ‘‘unnecessary
burden’’ to owners or operators affected
by the rules. Where there are differences
between this FIP and NSPS OOOO,
NDDoH requirements, and NDIC
requirements, they exist for a specific
reason. For example the requirements in
this FIP for produced oil and produced
water storage tanks provide legally and
practicably enforceable control
requirements for facilities currently
operating on the FBIR until applicable
storage tank requirements become
effective under NSPS OOOO. At that
time, the provisions in the NSPS OOOO
for produced oil and produced water
storage tanks will supersede the
produced oil and produced water
storage tank requirements in the FIP at
§ 49.4164(f), and owners or operators
will never be required to comply with
both sets of requirements since
duplicate requirements do not apply to
the affected equipment. In addition, we
are addressing emissions controls for
heater-treaters because we determined
such controls are cost effective and have
been demonstrated to be effective in
light of the air quality concerns at play
in the area. Specifically, we included
the provision in the FIP at
§ 49.4164(d)(2)(iii), which requires
aggregate storage tank VOC emissions at
any facility that are greater than 20 tpy
to be reduced by at least 98%, and VOC
emissions less than 20 tpy to be
controlled by at least 90%. We
evaluated and adopted this FIP
provision, which is consistent with the
requirements for the heater-treaters
found in the NDIC requirements at 38–
08–06.4 and the heater-treater
requirements in the Bakken Pool
Guidance. We acknowledge that the
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98% VOC DRE control requirement for
heater-treaters in this FIP is at the upper
end of the 90–98% range in the Bakken
Pool Guidance. However, the owners
and operators of oil and natural gas
production facilities on the FBIR have
indicated that a 98% VOC DRE is
achievable and committed in their
synthetic minor NSR applications to
reduce the mass content of VOC
emissions routed to the enclosed
combustors or utility flares used for
both produced gas from heater-treaters
and flashing gas from storage tanks by
at least 98%. With this reduction, the
owners and operators demonstrated that
for most of their facilities the potential
emissions would not trigger the
requirements to obtain a PSD and/or
Part 71 permit when accounting for the
requested federally enforceable
restrictions. The 98% level of control is
necessary because of the high volume of
VOC emissions that must be controlled.
The commenter did not specifically
state which ‘‘challenges’’ to NSPS
OOOO they were referring to in their
comment. However, current petitions
filed concerning NSPS OOOO are
outside of the scope of this rule.
Regardless of any future changes to
NSPS OOOO, the primary intent of FIP
is to provide environmental protection
on the FBIR by creating federally
enforceable control requirements for oil
and natural gas operations on the FBIR.
Additionally, as discussed above, these
FIP requirements are consistent with the
State’s requirements.
Comment: Multiple commenters
stated that completion and recompletion
requirements should be removed from
the FIP because completion and
recompletion requirements in NSPS
OOOO only apply to hydraulically
fractured natural gas wells, and that the
application of these activities to oil
wells in the FIP is therefore inconsistent
with NSPS OOOO.
Response: This FIP requires owners or
operators to route emissions from well
completion and recompletion
operations to a combustion device. This
is similar to the requirements for
hydraulically fractured gas wells in
NSPS OOOO prior to January 1, 2015.
While requirements for completions and
recompletions in the NSPS OOOO only
apply to natural gas wells, the FIP
includes this requirement for the oil and
natural gas wells on the FBIR because of
the high amount of associated natural
gas in the crude oil. This is a significant
source of VOC emissions that required
control in the FIP and we think such a
requirement is appropriate given the
emissions characteristics of these wells
in the Bakken formation, regardless of
the emissions characteristics of other oil
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and natural gas production wells
nationwide.
Comment: Commenter stated that the
EPA should require recompleted oil and
natural gas wells on the FBIR to perform
reduced emission completions (RECs).
The commenter asserted that many
states including Colorado and Wyoming
currently require RECs, and that both
states have thriving oil and natural gas
industries.22 The commenter also stated
that several natural gas companies
currently employ use of RECs despite
the fact that they are not required. The
commenter insisted that, if RECs are
determined not to be economical in
areas like the FBIR with limited natural
gas pipeline and gathering line
infrastructure, the EPA must find
alternative local uses for the natural gas.
Commenter stated that the EPA should
at least require RECs on the FBIR in the
near future, similar to the NSPS.
Commenter stated that the EPA’s NSPS
OOOO will require RECs at all new and
modified gas wells beginning in 2015.
Furthermore, another commenter stated
that if the FIP were to require green
completions, advanced notice of
completion or recompletion as is
included in the NSPS OOOO would be
a critical requirement in the FIP.
Response: RECs cannot be performed
if there is no gathering line available to
convey natural gas produced during the
completion flowback. Such lines are not
likely to be available if the well location
has no access to a natural gas gathering
system. Although pipeline
infrastructure is currently being
developed on the FBIR, we do not
believe there is currently sufficient
access to natural gas gathering pipelines
in all development areas of the FBIR to
require RECs at this time. We recognize
the potential for VOC emissions from
well completion and recompletion
operations and have maintained the
requirement in the final rule to reduce
these emissions by at least 90%. If we
determine at a later date that there is a
need for additional control of VOC
emissions from well completion and
recompletion operations, we may
propose additional FIPs or propose
supplements to this FIP.
Comment: One commenter stated that
the emission control requirements of the
FIP will not exceed the current NDIC
emission control requirements,
22 Commenter cites William C. Allison, Director,
Air Pollution Control Division, Colorado
Department of Public Health and the Environment,
Testimony before the United States Senate,
Environment and Public Works Committee, Clean
Air and Nuclear Safety Subcommittee, June 19,
2012. A copy of this transcript has been included
in the docket for the rule under Docket ID: EPA–
R08–OAR–2012–0479, which can be accessed at:
https://www.regulations.gov.
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Federal Register / Vol. 78, No. 56 / Friday, March 22, 2013 / Rules and Regulations
providing a ‘‘smooth transition’’ for the
owners or operators. Another
commenter requested more stringent
emission limits be required than the
NDIC requirements. A third commenter
expressed concern that the regulations
of the proposed FIP are equal to the
NDDoH regulations and noted that the
FBIR is its own nation, and therefore the
FIP regulations are pertinent to the
residents of the FBIR and not
individuals outside the FBIR’s
boundaries.
Response: One of the goals of this FIP
is to provide air quality protection for
the residents of the FBIR, while also
allow for continued development of
mineral resources. The FIP requirements
are consistent with the most relevant
aspects of the North Dakota rules based
on our evaluation that the level of
control was appropriate for meeting
these goals while ensuring the
enforceability required by a federal rule.
We also evaluated over 150 synthetic
minor NSR permit applications 23 to
identify the most significant sources of
VOC emissions and associated control
equipment employed by the operators to
ensure that the control requirements in
this FIP are based on the nature of oil
and natural gas production and storage
operations on the FBIR.
Comment: Several commenters stated
that the requirements of the FIP are too
stringent. The commenters also noted
that since FBIR is in attainment with all
applicable NAAQS, highly stringent
controls are neither appropriate nor
necessary. The commenters stated that
the 98% control required in the FIP is
above the 90–98% range the EPA
allowed in recent CAFOs. The
commenters also stated that the
requirements of the FIP are inconsistent
with the requirements that currently
apply to operators of the same type of
facilities through NDDoH regulations,
specifically the Bakken Pool Guidance.
The commenters asserted that the more
burdensome requirements of the FIP as
compared to those outside the FBIR may
discourage expansion of operations
within the FBIR.
On the other hand, other commenters
stated their support of the EPA’s
requirements in the FIP, and encouraged
the EPA to retain the 98% VOC DRE
requirement for flaring at storage tanks,
restating the EPA’s position that this
level is appropriate considering the
unique geochemistry of the Bakken
formation.
23 The information reviewed was contained in
synthetic minor NSR applications submitted to
EPA, which are included in the docket for this rule
under Docket ID: EPA–R08–OAR–2012–0479,
which can be accessed at: https://
www.regulations.gov.
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Response: We disagree that the
requirement to reduce VOC emissions
from production and storage operations
by 98% is too stringent or burdensome.
The owners and operators of oil and
natural gas production facilities on the
FBIR have indicated that a 98% VOC
DRE is achievable and have even
committed to it in their synthetic minor
NSR applications to reduce the mass
content of VOC emissions routed to the
enclosed combustors or utility flares
used for both produced gas from heatertreaters and flashing gas from storage
tanks by that amount. The high VOC
content of the oil and natural gas
produced from Bakken Pool operations
allows for a higher DRE. Many of the
owners and operators of oil and natural
gas production facilities indicated that a
DRE of 98% was imperative to limit the
applicability of permitting requirements
that may result if only a 90% creditable
reduction of VOC emissions is allowed.
We also evaluated regulations in other
oil and natural gas producing states
within Region 8 and note that this FIP
is consistent with Wyoming’s
requirements to control both storage
tank and separation vessels by 98%.
Comment: Multiple commenters
expressed concern with the
requirements in § 49.4164 which states
that, beginning with the first date of
production, facilities subject to the rule
are required to route natural gas
emissions from production operations
and storage operations to a 90%
emissions reduction device. Within 90
days of the first date of production, this
device must be either replaced with a
98% emissions reduction device or tied
to a gas sales line. The 90-day time
frame listed in the rule should be
extended to at least 180 days, to allow
operators time to get the required
equipment. There is added concern that
given the number of devices that may
need to be purchased for new facilities,
particularly with the impending
implementation of NSPS Subpart
OOOO, equipment shortages will be
expected. Further, commenters stated
that the EPA should include a provision
here that allows for an extension of the
180-day time limit for upgrading to a
sales line or 98% control device in the
event such equipment is unavailable.
Response: We disagree with the
commenter that we should change the
90-day timeframe allotted to either
replace a 90% emissions reduction
device with a 98% emissions reduction
device or inject produced natural gas
and natural gas emissions to a gas sales
line. One of the goals of this FIP is to
protect human health and the
environment and the required VOC
emission control should be achieved as
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expeditiously as possible. Furthermore,
when evaluating the estimated
emissions provided by the oil and
natural gas production operators for the
facilities covered by the August 2011
CAFOs (77 FR 48879), we found that in
many cases, the difference in controlled
heater-treater emissions between only
90% VOC DRE for 90 days or less versus
more than 90 days is the difference
between being a true minor source of
VOC emissions under the Federal Tribal
NSR regulations and being a major
source of VOC emissions under the PSD
regulations based on the high VOC
emissions from these oil and natural gas
operations on the FBIR.
We recognize that some owners and
operators might need time to acquire
equipment that achieves the required
VOC control and we believe, based on
the information in permit applications
provided by the owners and operators
on the FBIR that 90 days is a reasonable
timeframe to acquire the necessary
control equipment. The interim final
FIP contains a provision that the owner
or operator may use 98% VOC DRE
control devices other than those
specified in the FIP upon prior written
approval from the EPA. Based on
information submitted to date by an
operator requesting alternative control
device approval, it is possible to
economically engineer shop-built flares
that can be demonstrated to meet the
required VOC DRE and that can be used
until a utility flare becomes available, if
insertion of the produced natural gas to
a sales pipeline or use of the produced
natural gas for other beneficial purpose
is demonstrated to not be feasible.24
F. Monitoring and Recordkeeping
Requirements
Comment: Multiple commenters
stated that the EPA should impose less
burdensome monitoring and
recordkeeping requirements for minor
sources. The commenters asserted that
the level of detail required in the FIP is
generally required only for major
sources, and that it is higher than the
detail required for minor sources by
NDDoH regulations and the Bakken Pool
Guidance. The commenters stated that
the FIP should mirror NDDoH
regulations regarding heater-treater
control devices, meaning that
monitoring and recordkeeping
requirements should be eliminated. The
commenters stated that the cost of
monitoring and recordkeeping in the
24 A copy of the submittal from Lisa Decker, WPX
Energy, to Carl Daly, EPA Region 8 Air Program
Director, on November 13, 2012 has been added to
docket for the rule under Docket ID: EPA–R08–
OAR–2012–0479, which can be accessed at: https://
www.regulations.gov.
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FIP is high compared to the benefit, and
that these factors will create a
disincentive to expand drilling on the
FBIR. Although one commenter stated
that the EPA’s monitoring and reporting
requirements are reasonable and will
facilitate compliance while also
gathering pertinent information on
operations. Yet another commenter
stated that the EPA’s monitoring and
reporting requirements could be even
more stringent to include leak
monitoring of the closed vent systems
and advanced notification prior to
performing a well completion or
recompletion.
Response: We acknowledged in the
Federal Register notice and the TSD for
the interim final FIP that monitoring,
reporting, and recordkeeping (MRR)
requirements were an area where the
FIP would differ from the NDIC and
NDDoH regulations, and the Bakken
Pool Guidance. Federal regulations must
contain requirements that are legally
and practicably enforceable; and
therefore this FIP contains legally and
practicably enforceable provisions that
are necessary to meet the requirements
for federal regulations. Recognizing that
this FIP regulates different oil and
natural gas production equipment than
NSPS OOOO, the approach we took in
developing MRR requirements for oil
and natural gas production emission
control equipment is similar to the
approach the Agency used in
developing MRR requirements for gas
well production emission control
equipment. Therefore, we do not believe
the requirements are any more
burdensome than requirements for
similar equipment in NSPS OOOO.
Comment: Several commenters stated
that the EPA should allow an operator
to make a visual inspection only once
per quarter, and should require that
operator to conduct a one-hour Method
22 evaluation only if the control device
is actually smoking. The commenters
asserted that the amount of time it
would take just to conduct quarterly
monitoring without this change could
potentially require three full-time
equivalent operators for that task alone.
The commenters requested that the
EPA make two additional changes to the
FIP’s current requirements for
monitoring smoking combustion
devices, though the commenters
ultimately stated that the resource
burden to meet the smoke monitoring
requirements would still be extreme
regardless of whether the two changes
were made. The first change is that the
EPA increase the amount of time a
control device can smoke before being
considered a ‘‘smoking’’ device from
two minutes to five minutes for
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consistency.25 The second change is that
the EPA remove the phrase ‘‘whenever
an operator is on site’’ from
§ 49.4166(g)(3). The commenter stated
that this phrase is ambiguous when read
in conjunction with the phrase ‘‘at a
minimum quarterly.’’ The commenters
also stated that it would be extremely
burdensome for an operator to observe
a flare for an entire hour each time that
operator was on site. The commenters
ultimately stated that even with this
change, the requirement would still be
extremely burdensome.
Response: We agree with the
commenters that the EPA should only
require an operator to conduct a Method
22 evaluation if visible smoke emissions
are observed. We also agree with the
commenter’s request that we increase
the amount of time a control device can
smoke before being considered a
‘‘smoking’’ device from two minutes to
five minutes. This is consistent with the
specification in NSPS OOOO at
§ 60.5415(e)(vii)(C) and (e)(vii)(D)(3),
and the general provisions at § 60.18(b)
for visible emissions testing of
combustion control devices (77 FR
49556). However, we do not agree that
one-hour observations are suitable, as
both § 60.18(b) and NSPS OOOO require
two-hour observations and we have no
reason to conclude that a different
approach is appropriate here.
We have revised the applicable
condition in this final FIP to require the
owner or operator to monitor for visible
smoke and to only conduct a Method 22
evaluation if visible smoke emissions
are observed. We have also revised the
provision to specify that visible smoke
emissions are present if smoke is
observed more than five minutes in any
2 consecutive hours. We have not
removed the requirement to conduct on
site inspections of the operation of the
device when an operator is onsite, but
not less frequently than quarterly,
because we disagree that this
requirement is ambiguous. In addition,
since we changed the monitoring
provision to require observations for
visible smoke before triggering the
requirement for Method 22 evaluations,
the commenters’ concern that the
requirements are burdensome has been
addressed.
Comment: Several commenters stated
that the EPA should allow the operator
to make frequent onsite checks or use
other alternatives to meet the
continuous recording device
requirement in § 49.4165(c)(6)(v) for
utility flares and enclosed combustors.
The commenters asserted that there are
25 Commenter does not list the rule with which
such a change would maintain consistency.
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significant challenges with obtaining the
appropriate continuous monitoring
equipment, and that operator checks
should therefore be accepted as fully
meeting the requirement, or at least as
meeting the requirement in the interim.
Response: We agree that there needs
to be an opportunity to perform
alternative monitoring upon prior
written EPA approval. We have revised
the applicable provision at § 49.4166(i)
to reflect this in the final rule.
Comment: One commenter stated that
the EPA should ‘‘require regulated
entities to regularly monitor VOC
emissions from the components of
closed-vent systems, using wellestablished methods and leak
thresholds.’’ The commenter stated that
in the preamble and proposed
regulatory text, the EPA required proper
maintenance and operation of vent
lines, connections, fittings, valves, relief
valves, or any other appurtenance
employed to contain, collect and
transport gases, and required that these
components be designed to operate with
no detectable natural gas emissions (77
FR 48889, 48896). However, the EPA
failed to require producers to
demonstrate or verify that the required
closed-vent systems are ‘‘maintained
and operated properly’’ or ‘‘operate with
no detectable natural gas emissions.’’
Commenter stated that without a
monitoring or verification requirement,
the requirements for closed-vent
systems ‘‘will be unenforceable and
largely hortatory in nature.’’
Commenter also stated that the lack of
monitoring or verification requirements
for closed-vent systems is at odds with
the goal of the FIP, which is to establish
emission limits at oil and natural gas
facilities that are legal and practically
enforceable. Commenter asserted that
absent these verification requirements, a
producer could not guarantee natural
gas is controlled at 90% or 98%, and the
EPA could not guarantee that the
projected emission reductions have
been achieved. Commenter stated that
the EPA requires closed-vent monitoring
techniques in other regulations,
including NSPS OOOO and the
‘‘National Uniform Emission
Standards.’’ 26 Commenter
recommended that, at a minimum, the
EPA use the approach proposed by the
agency in the National Uniform
Emission Standards.
26 ‘‘National Uniform Emission Standards for
Storage Vessel and Transfer Operations, Equipment
Leaks, and Closed Vent Systems and Control
Devices; and Revisions to the National Uniform
Emission Standards General Provisions,’’ 77 FR
17,898, 17,943 and 18,009 (proposed Mar. 26, 2012)
(proposed 40 CFR 65.429(a)).
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Response: We disagree that leak
detection and repair (LDAR)
requirements should be included in this
FIP. As discussed in the preamble and
TSD for NSPS OOOO, it was determined
that LDAR monitoring was not cost
effective for smaller oil and natural gas
production facilities and we have no
information from which to conclude
that the same is not the case here. To
demonstrate compliance with the
requirements for closed-vent systems,
the final rule requires all vent lines,
connections, fittings, valves, relief
valves, or any other appurtenance on
tank covers and closed-vent systems be
maintained and operated properly at all
times and that they are visually
inspected at least quarterly while the
equipment is operating. Further, each
bypass devices on all closed-vent
systems are required to be equipped
with a flow meter to continuously
monitor the volume of natural gas
emissions that are diverted from the
natural gas gathering pipeline, or
required control device. The final rule
requires that the owners and operators
keep records of all monitoring
parameters and report instance where
construction and operation was not
performed in compliance with the
requirements specified in the final rule.
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G. Reporting Requirements
Comment: Commenter recommended
that the EPA require a self-certification
mechanism, which would require a
senior company official to certify as to
the truth, accuracy and completeness of
its annual report. Commenter suggested
that the EPA draw on the example of the
NSPS OOOO in developing this
mechanism.
Response: We agree that selfcertification is an important mechanism
for assuring the public that the
information submitted by each facility is
accurate and have added a provision in
the rule requiring owners or operators to
certify as to the truth, accuracy and
completeness of the annual reports. The
EPA already requires a similar
certification in the NSPS OOOO;
therefore, we concluded that it is not
unreasonable to require the certification
for reports submitted under this FIP.
H. Cost Analysis
Comment: One commenter agreed
with the EPA’s position that the FIP
does not impose a significant cost on
operators. Another commenter noted the
benefits of the FIP, specifically citing
the substantial and cost-effective VOC
reductions that the EPA estimated in the
FIP.
Response: We acknowledge the
support of these commenters for this
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FIP. We have included information
regarding the cost-effectiveness of this
FIP in the TSD for the interim final
rule.27
Comment: Commenter stated that the
EPA does not address the economic
benefits of natural gas capture when
estimating the costs and benefits of the
FIP. The commenter stated that
‘‘producers are very likely to derive
substantial amounts of revenue by
installing vapor recovery units and
gathering lines to route excess natural
gas that is captured by voluntary RECs
and through other regulatory
requirements to reduce leaks.’’ The
commenter referenced an NRDC
report 28 and the NSPS OOOO (77 FR
49534, 49537) to support this point. The
commenter also stated that the EPA
noted this revenue opportunity in the
FIP TSD, though it did not address it in
the FIP itself. The commenter stated that
it is especially important to consider
these benefits because the EPA notes
that its analysis already overestimates
costs, and also generally stated that gas
is a valuable commodity that should not
be wasted.
Response: We did not discuss the use
of RECs in the cost analysis in the TSD,
as there is not currently adequate access
to pipeline gathering systems on the
FBIR to require RECs from well
completion and recompletion
operations, thus the current
infrastructure is not amenable to this
technique at this time. However, if we
determine at a later date that there is a
need for additional control of VOC
emissions during oil and natural gas
production well completion and
recompletion operations on the FBIR,
we may propose additional FIPs or
propose supplements to this FIP.
Comment: Commenter stated that the
EPA failed to quantify the economic
benefits of protecting public health and
ecosystems from pollution in the FIP.
Commenter stated that increased oil and
natural gas production leads to
increased levels of ozone in the
surrounding area, risking public
health.29 Commenter stated that the EPA
27 The TSD includes a more detailed explanation
of the cost analysis for this FIP. It can be found in
the docket for this rule, Docket ID: EPA–R08–OAR–
2012–0479, which can be accessed at: https://
www.regulations.gov.
28 ‘‘Natural Resources Defense Council, Leaking
Profits: The U.S. Oil and Gas Industry Can Reduce
Pollution, Conserve Resources, and Make Money by
Preventing Methane Waste,’’ 2012. A copy of this
document has been included in the docket for this
rule under Docket ID: EPA–R08–OAR–2012–0479,
which can be accessed at: https://
www.regulations.gov.
29 Commenter provides several examples in
which oil and gas development drives up ozone
emissions. See NRDC comments in the docket for
this rule for specific citations.
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17849
must consider the medical and other
public health costs associated with oil
and natural gas production and
resulting ozone in order to provide an
accurate economic impact assessment
for the FIP.
Response: Given the accelerated
development in this area, the high VOC
emissions associated with the oil and
natural gas operations and the absence
of infrastructure on the FBIR, we
determined the FIP should be effective
immediately upon promulgation to
ensure the protection of public health
and the environment from exposure to
air pollution, avoid fire hazards and
protect the public from hazardous
conditions. This FIP establishes
regulations that significantly reduce
VOC emissions from oil and natural gas
production facilities on the FBIR,
thereby protecting public health and the
environment. This FIP is not a
significant regulatory action under
Executive Order 12866 and therefore an
analysis of the potential costs and
benefits associated with this action is
not required. While we did not
specifically quantify the economic
benefits of protecting public health and
the environment in the cost analysis, the
control equipment required by this FIP
is already extremely cost effective at less
than $15/ton, and any additional cost
benefits due to possible reduced public
health costs would only result in
increased cost effectiveness. Therefore,
we believe the cost analysis sufficiently
addresses the economic impacts for this
action.
I. Public Notice
Comment: A commenter stated that
the EPA did not provide the public with
proper notice of the hearing, and
therefore failed to ensure public
participation in the rulemaking process.
The commenter stated that the notice of
the hearing in the tribal newspapers
mistakenly referred to the hearing as a
‘‘meeting,’’ which the commenter noted
is quite different than a hearing. The
commenter also stated that information
about the hearing should have been
advertised on the radio, and noted that
many residents in the FBIR have limited
internet access. Some commenters
blamed lack of adequate notice on what
they observed to be a low turnout at the
hearing(s). One commenter stated that
the oil companies had been given
adequate notice, but the public had not.
One commenter urged the EPA to come
back and host more hearings. Several
commenters requested an extension of
the comment period, but none specified
a suggested length of extension.
Response: We disagree with these
comments. We have exceeded the CAA
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public notice requirements for
rulemaking. Under Section 307, the EPA
is required to allow any person to
submit written comments, data, or
documentary information, as well as
give interested persons an opportunity
for the oral presentation of data, views,
or arguments. The EPA is required to
keep a transcript of any oral
presentations and keep the record of the
proceeding open for 30 days after
completion of the proceeding to provide
an opportunity for submission of
rebuttal and supplementary
information. The EPA is required to
allow a reasonable period of at least 30
days for public participation.
As explained earlier in this notice, in
promulgating this rule, the EPA is
exercising its discretionary authority
under sections 301(a) and 301(d)(4) of
the CAA to promulgate regulations as
necessary to protect tribal air resources.
Therefore, while the Title I planning
requirements of the CAA applicable to
states do not directly apply to the EPA
in promulgating a FIP in Indian
Country, the EPA used the public notice
requirements found within the planning
requirements as a guide in developing
this FIP. For this FIP, the EPA also
followed the public hearing and public
notice regulations in 40 CFR 51.102 as
a guide. According to CAA sections
301(a) and 301(d)(4) and 40 CFR 51.102,
notice given to the public is to be
provided by prominent advertisement in
the affected area announcing the date(s),
times(s), and place(s) of such hearings.
Each proposed plan is to be made
available for public inspection in at
least one location in each region that it
will apply.
The proposed FIP was published in
the Federal Register on August 15,
2012. The Federal Register notice stated
that public hearings would be held on
September 12, 2012 from 1–4 p.m. and
again at 6–8 p.m. at the 4 Bears Casino
and Lodge in New Town, ND. An
address for the location and contact
information was provided. The Federal
Register notice provided for a 60-day
comment period, which required that
public comments be received by the
EPA Region 8 by October 15, 2012 and
provided instructions for submitting
comments. Two locations for review of
publically available supporting docket
materials for this FIP were listed
including one at the EPA Region 8 office
in Denver and one at the Environmental
Division office of the Three Affiliated
Tribes of the Mandan, Hidatsa, and
Arikara Nation, in New Town, ND. A
link for publically available electronic
docket materials was listed in the
Federal Register notice.
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A public notice was posted in the
following newspapers regarding the
availability of this FIP for public
comment on August 15 and 17, 2012:
Bismarck Tribune, Dickinson Press,
Minot Daily News, New Town News,
Williston Herald, MHA Times, and
Mountrail County Record. This public
notice included all of the information
about the public hearings, docket review
locations (including internet link),
contact information, and the
instructions for submittal of comments
that was contained in the Federal
Register notice. Additionally, this
public notice listed seven locations and
addresses where the public could
review copies of this FIP and all
supporting docket materials in addition
to the two listed in the Federal Register
notice, including: Three Affiliated
Tribes of the Mandan, Hidatsa, and
Arikara Nation’s Administration Office,
New Town, ND; Fort Berthold
Community College Library, New Town,
ND; Mandaree Community Center,
Mandaree, ND; Parshall Segment Office,
Parshall, ND; Twin Buttes Memorial
Hall, Halliday, ND; White Shield
Segment Office, Roseglen, ND; and Four
Bears Community Building, Four Bears
Village, ND. The EPA confirmed that
this public notice was published in each
of the seven local newspapers. We
confirmed that copies of the FIP and
administrative records were received on
August 13, 2012 by each of the nine
locations listed above.
We also prepared a public notice and
request for comment bulletin. A copy of
the bulletin was provided to the
Director of the Three Affiliated Tribes of
the Mandan, Hidatsa, and Arikara
Nation Environmental Programs Office
in New Town, ND on August 10, 2012
with a request that it be posted in
prominent locations throughout the
Reservation and affected area. The
bulletin provided a summary of the
proposed rule, the contacts, the nine
locations where the proposed rule and
administrative records could be viewed,
the date, times and location of the
public hearings and referred the public
to a link for publically available
electronic docket materials.
Additionally, we prepared a Public
Service Announcement (PSA) for the
local radio station, KMHA 91.3 FM
Radio, Fort Berthold, New Town, ND. A
copy of the PSA was provided to the
Director of the Three Affiliated Tribes of
the Mandan, Hidatsa, and Arikara
Nation Environmental Programs Office
in New Town, ND on August 10, 2012
with a request that it be provided to the
local radio station for broadcasting
throughout the Reservation and affected
area. The PSA provided a brief summary
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of the proposed rule, requested public
comment through October 15, 2012,
provided a contact, listed the eight
locations on the FBIR where the
proposed rule and administrative
records could be viewed, and provided
date, time(s) and location information
for the September 12, 2012 public
hearings. One of the commenters noted
the PSA was aired on the local radio
station. This is documented on Page 30
of the public hearing transcript for
September 12, 2012 at 6 p.m.
Transcripts for both public hearings
held on September 12, 2012 were
generated and placed into the docket for
this FIP. The comment period was kept
open for 30 days after the public
hearing. We verified that the seven
newspaper notices published on August
15 and 17, 2012 referenced the public
hearings held on September 12, 2012 as
‘‘public hearing’’ and not as a ‘‘public
meeting.’’ This included the New Town
News and the MHA Times in New
Town, ND. The commenter may have
intended to refer to the PSA instead of
the newspaper regarding reference to a
‘‘public meeting’’ instead of a ‘‘public
hearing.’’ The PSA inadvertently
referred to the ‘‘public hearing’’ as a
‘‘public meeting.’’
These opportunities for public
participation were provided equally to
the public and the regulated
community. All residents and the
regulated community were given the
same opportunities to request and
access information, comment and
participate in this rule making process.
Based on the Federal Register notice,
newspaper notices, posting public
notice and request for comment bulletin
at locations on the reservation, holding
two public hearings, making public
hearing transcripts publically available,
providing a 60-day public comment
period, PSA, and links for publically
available electronic docket materials,
the EPA has exceeded all legal
requirements for proper public notice of
this FIP. We therefore decided not to
hold additional hearings and meetings,
or extend the public comment period.
Comment: Another commenter stated
that the lack of adequate public notice
was not compliant with environmental
justice.
Response: We disagree with this
comment. Environmental justice is one
of the Agency’s highest priorities and
we believe the process used in
developing this rule fully complies with
the requirements of Executive Order
12898 (59 FR 7629, February 16, 1994),
which establishes federal executive
policy on environmental justice (EJ). Its
main provision directs federal agencies,
to the greatest extent practicable and
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permitted by law, to make EJ 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 defines environmental
justice as providing fair treatment and
meaningful participation in
environmental decision making. As
detailed above, EPA exceeded CAA
public notice requirements for
rulemaking, and the record reflects
extensive efforts to ensure meaningful
participation in this case. The EPA’s
Action Development Process, Interim
Guidance for Considering
Environmental Justice during the
Development of an Action provides
additional guidance for implementation
of EO 12898 related to public notice for
actions like rulemaking. This guidance
suggests inclusion of one or more public
meetings or hearings in or near affected
communities and tribes. Public
meetings or hearings should include
sufficient notice and should be
scheduled at a time and place
convenient to the affected communities
and tribes. Successful solicitation of
public comments from affected
communities and tribes may incorporate
tailored outreach materials that are
concise, understandable, and readily
accessible to the communities to be
reached. For remote towns and villages,
local radio stations, local newspapers,
and posters at village or community
centers may represent the most effective
approach. We employed these methods
to ensure that we reached the FBIR EJ
community and allowed for meaningful
involvement of affected communities
and tribes.
While we understand that many
residents on the FBIR do not have
internet access, we employed numerous
prominent advertisement methods not
relying on the internet, including
newspaper notices, posting public
notice and request for comment bulletin
at locations on the FBIR, holding public
hearings, providing a 60-day public
comment period, providing a PSA
broadcast on local radio, as well as
relying on the internet by providing
links for publically available electronic
docket materials.
We conclude that the public notice
process exceeded EPA’s legal
obligations in rulemakings of this type,
and that there is no reason to believe
that such public notice was inadequate
for compliance with the Executive
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Order.30 Although we agree that turnout
was low at the September 12, 2012
public hearings, we do not believe that
additional public hearings or meetings
would have significantly increased
turnout. We believe that low turnout at
the public hearings was due to factors
other than the significant public notice
methods employed. We employed every
reasonable effort to encourage
attendance at public hearings and obtain
public comments on this FIP.
We recognize that there are EJ
concerns in the FBIR community. We
have determined that this rule will not
have disproportionately high and
adverse human health or environmental
effects on minority, low-income, and
indigenous populations, because it
ensures compliance with the NAAQS,
which provides environmental and
public health protection for all affected
populations. Compliance with the
NAAQS is relevant to an EJ claim to the
extent that the NAAQS are health-based
standards, designed to protect public
health with an adequate margin of
safety, including sensitive populations
such as children, the elderly, and
asthmatics.
Comment: A commenter asked if the
annual report of FBIR facility activity
would be accessible by the public.
Response: These reports will be
submitted to the EPA Region 8 office in
Denver, Colorado and maintained on
file and will be available to the public.
The documents may be obtained
through the Freedom of Information Act
(FOIA) process. If you seek a record, you
should address your request to the EPA
Region 8 FOIA Office. Requests for
records can be sent by mail to FOIA
office at Regional Freedom of
Information Officer; U.S. EPA, Region 8,
Mailcode: 8–OC; 1595 Wynkoop Street;
Denver, CO 80202–1129. Request may
also be made by electronic mail to
r8foia@epa.gov, by facsimile at (303)
312–6859, or by telephone at (303) 312–
6856. Your request should be as specific
as possible with regard to the subject,
time frames, and locations. You do not
have to give a requested record’s name
or title, but the more specific you are;
the more likely it will be that the record
you seek can be located. For example,
if you are seeking records dealing with
the FIP annual reports, request the FBIR
30 See In re Shell Gulf of Mexico, Inc. & Shell
Offshore, Inc., 15 EAD __, OCS Appeal Nos. 11-02,
11-03, 11-04, 11-08, slip op. at 40 n. 38 (EAB Jan.
12, 2012) (treating evidence of compliance with
statutory and regulatory public participation
requirements as showing sufficiency of
participation for purposes of compliance with EO).
A copy of the document has placed in the docket
for this rule under Docket ID: EPA–R08–OAR–
2012–0479, which can be accessed at: https://
www.regulations.gov.
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FIP Annual Reports, the owner or
operator you seek information on, and
the calendar year(s) for the reports you
seek.
V. Summary of Final Rule and
Significant Changes from the Proposed
and Interim Final Rule
A. Administrative Edits
Correction: In the proposed rule we
identified incorrect citations to the Code
of Federal Regulations (CFR) for
publishing the rule. The final rule has
been promulgated at Subpart K of 40
CFR part 49 which is specific to Region
8 FIPs.
§ 49.140 is now § 49.4161;
§ 49.141 is now § 49.4162;
§ 49.142 is now § 49.4163;
§ 49.143 is now § 49.4164;
§ 49.144 is now § 49.4165;
§ 49.145 is now § 49.4166;
§ 49.146 is now § 49.4167; and
§ 49.147 is now § 49.4168.
B. Introduction
This rule applies to any person who
owns or operates an existing
(constructed or modified on or after
August 12, 2007), new, or modified oil
and natural gas production facility 31
that is located on the FBIR and
producing from the Bakken Pool with
one or more oil and natural gas wells,
any one of which a well completion or
recompletion operation is/was initiated
on or after August 12, 2007.
For the purposes of this rule, a well
completion means the process that
allows for the flowback of oil and
natural gas from newly drilled wells to
expel drilling and reservoir fluids and
tests the reservoir flow characteristics,
which may vent produced hydrocarbons
to the atmosphere via an open pit or
tank. A well completion operation
means any oil and natural gas well
completion with hydraulic fracturing
occurring at an oil and natural gas
production facility. The completion date
is considered the date that construction
at an oil and natural gas production
facility has commenced. The
recompletion date is considered the date
that a modification has occurred at an
oil and natural gas production facility.
The reason we selected the initiation of
completions operations as the date for
defining a new facility is that owners
and operators use drill rigs prior to
31 For the purposes of this rule, an oil and natural
gas production facility consists of one or more oil
and natural gas wells and the air pollution emitting
units that are utilized for production operations and
storage operations for those wells. This definition
was clarified from what was proposed in the
interim final rule. Additionally, August 12, 2007 is
the earliest well completion date identified in the
CAFOs.
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initial completion operations and this
equipment is generally not in one
location long enough to be considered a
stationary source. In addition, it is not
certain during the drilling operations
whether a well will be a producing well.
Hence, it is not known whether an oil
and natural gas production facility will
be constructed to support that well. The
outcome of a completion operation
provides the well owners and operators
information necessary to determine
whether an oil and natural gas
production facility will be constructed.
Clarification: We have added
language to the introduction at
§ 49.4161(b) to clarify that, for the
purposes of this rule, the initiation of
well completion operations and well
recompletion operations are the dates
that construction and modifications
commence, as set forth in the regulatory
text of this final rule.
Compliance with the rule is required
no later than June 20, 2013 or upon
initiation of well completion or
recompletion operations, whichever is
later. Upon signature by the
Administrator, we will post this rule on
our internet site (https://www.epa.gov/
region8/air/fbirfip.html) and notify the
owners and operators and the Three
Affiliated Tribes of the Mandan,
Hidatsa, and Arikara Nation.
Clarification: We have changed the
language in the introduction at
§ 49.4161(c) to clarify that the
compliance date is upon initiation of
well completion operations and well
recompletion operations, as follows:
‘‘§ 49.4161(c) When must I comply with
§§ 49.4161 through 49.4168?
Compliance with §§ 49.4161 through
49.4168 is required no later than June
20, 2013 or upon initiation of well
completion operations or well
recompletion operations, whichever is
later.’’
C. Provisions for Delegation of
Administration to the Three Affiliated
Tribes of the Mandan, Hidatsa, and
Arikara Nation
The provisions in § 49.4162 establish
the steps by which the Three Affiliated
Tribes of the Mandan, Hidatsa, and
Arikara Nation may request delegation
to assist us with the administration of
this rule and the process by which the
Regional Administrator of the EPA
Region 8 may delegate to the Tribes the
authority to assist with such
administration of this rule. As described
in the regulatory provisions, any such
delegation will be accomplished
through a delegation of authority
agreement between the Regional
Administrator and the Three Affiliated
Tribes of the Mandan, Hidatsa, and
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Arikara Nation. This section provides
for administrative delegation of this
federal rule and does not affect the
eligibility criteria under CAA section
301(d) and 40 CFR 49.6 for TAS should
the Tribes decide to seek such treatment
for the purpose of administering their
own EPA-approved program under
tribal law. Administrative delegation is
a separate process from TAS under the
TAR. Under the TAR, Indian tribes seek
EPA-approval of their eligibility to run
CAA programs under their own laws.
The Three Affiliated Tribes of the
Mandan, Hidatsa, and Arikara Nation
would not need to seek TAS under the
TAR for purposes of requesting to assist
us with administration of this rule
through a delegation of authority
agreement. In the event such an
agreement is reached, the rule would
continue to operate under federal
authority throughout the FBIR, and the
Tribes would assist us with
administration of the rule to the extent
specified in the agreement.
D. General Provisions
The provisions in § 49.4163 General
Provisions provide: (1) Definitions that
apply to this rule; (2) assurance that we
will maintain its authority to require
testing, monitoring, recordkeeping, and
reporting in addition to that already
required by an applicable requirement,
in a permit to construct or permit to
operate in order to ensure compliance;
and (3) assurance that nothing in the
rule will preclude the use, including the
exclusive use, of any credible evidence
or information, relevant to whether a
facility would have been in compliance
with applicable requirements if the
appropriate performance or compliance
test had been performed.
E. Construction and Operational Control
Measures
The provisions in § 49.4164
Construction and Operational Control
Measures provide requirements to
reduce VOC emissions during well
completion and recompletion
operations. The owner or operator must
route all casinghead natural gas
emissions associated with completion
and recompletion operations to a utility
flare or a pit flare capable of reducing
the mass content of VOCs in the natural
gas vented to it by at least 90.0%. We
note that the well completion and
recompletion control requirements to
use pit flares or utility flares that have
the capability to reduce the mass
content of VOC in the natural gas
emissions routed to them by at least
90.0% percent by weight are the
minimum level of control that will be
allowed under this rule. Owners and
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operators may also choose to perform
reduced emission completions and
recompletions 32, which would exceed
the 90.0% VOC emission reduction
requirement. This section also requires
the control of production and storage
operations and imposes a timeline for
installation of the controls on these
operations. The owner or operator is
required to reduce the mass content of
VOC emissions from natural gas during
oil and natural gas production and
storage operations by at least 90.0%
percent on the first date of production.
Within 90 days of the first date of
production, we require the owner or
operator to route the natural gas from
the production and storage operations
through a closed-vent system to a utility
flare or equivalent combustion device
capable of reducing the mass content of
VOC in the natural gas vented to the
device by at least 98.0%. The owner or
operator also has the option to design
their production and storage operations
to recover the natural gas as product and
inject it into a natural gas gathering
pipeline system for sale or other
beneficial purpose. For those owners or
operators that choose to capture the
natural gas as product rather than a
pollutant to be controlled, the natural
gas may temporarily be routed through
a closed-vent system to an enclosed
combustor, utility flare or pit flare in
instances where injection of the product
into the pipeline is temporarily
infeasible. In these situations, the pit
flare is considered a backup standby
unit used for unplanned flare events,
such as during temporarily limited
pipeline capacity, that are beyond a
producer’s control and the pit flare is
used to safely burn the natural gas
product that could otherwise pose a
potential risk to workers, the
community, or the environment. The
owner or operator, however, must limit
the use of the pit flare in these instances
to 500 hours in any consecutive 12month period.
The rule requires the owner or
operator to route all standing, working,
breathing and flashing losses from the
produced oil storage tanks and any
produced water storage tanks
interconnected with the produced oil
storage tanks through a closed vent
system to either an operating system
32 U.S. Environmental Protection Agency. Lessons
Learned from Natural Gas STAR Partners: Reduced
Emissions Completions for Hydraulically Fractured
Natural Gas Wells. Office of Air and Radiation:
Natural Gas Star Program. Washington, DC.
Available at: https://epa.gov/gasstar/documents/
reduced_emissions_completions.pdf. Accessed July
26, 2012. A copy of this document has been placed
in the docket for this rule under Docket ID: EPA–
R08–OAR–2012–0479, which can be accessed at:
https://www.regulations.gov.
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designed to recover and inject the
natural gas emissions into a natural gas
gathering pipeline system for sale or
other beneficial use, or to an enclosed
combustor or utility flare capable of
reducing the mass content of VOC in the
natural gas emissions vented to the
device by at least 98.0%. However, to
prevent duplicative federal
requirements for owners and operators
of storage tanks on the FBIR subject to
both this rule and NSPS OOOO, storage
tanks subject to and controlled under
the requirements specified in 40 CFR
part 60, subpart OOOO are considered
to meet the storage tank control
requirements of this rule. No further
requirements apply for such storage
tanks under this rule. In addition, the
rule provides that if the uncontrolled
PTE of VOCs from the aggregate of all
produced oil storage tanks and
produced water storage tanks
interconnected with produced oil
storage tanks at an oil and natural gas
production facility is less than, and
reasonably expected to remain below,
20 tons in any consecutive 12-month
period, then the owner or operator may
use a utility flare or enclosed combustor
that is capable of reducing the mass
content of VOC in the natural gas
emissions vented to the device by only
90.0% upon prior written approval by
the EPA.33
The control devices must be operated
under specific conditions as specified in
§ 49.4165 Control Equipment
Requirements and § 49.4166 Monitoring
Requirements.
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F. Control Equipment Requirements
The provisions in § 49.4165 Control
Equipment Requirements require the
use of covers on all produced oil and
water storage tanks and the use of
closed-vent systems with all VOC
capture and control equipment. Section
49.4165 also specifies construction and
operational requirements for the covers
and closed-vent systems. In addition,
§ 49.4165 requires specific construction
and operational requirements of pit
flares, enclosed combustors, and utility
flares.
The provisions in § 49.4165 require
that each owner and operator equip the
openings on each produced oil storage
tank and each produced water storage
tank that is interconnected with
produced oil storage tanks with a cover
that ensures that natural gas emissions
are efficiently routed through a closedvent system to a vapor recovery system
33 If the owner or operator receives written
approval for a new method from the EPA, the owner
or operator must calculate potential to emit based
on the new EPA-approved method.
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an enclosed combustor, or a utility flare.
Each cover and all openings on the
cover (e.g., access hatches, sampling
ports, and gauge wells) must form a
continuous barrier over the entire
surface area of the produced oil and
produced water in the storage tank.
Each cover opening must be secured in
a closed, sealed position (e.g., covered
by a gasketed lid or cap) whenever
material is in the tank on which the
cover is installed except during those
times when it is necessary to use an
opening as follows: (1) To add material
to, or remove material from the unit
(this includes openings necessary to
equalize or balance the internal pressure
of the unit following changes in the
level of the material in the unit); or (2)
to inspect or sample the material in the
unit; or to inspect, maintain, repair, or
replace equipment located inside the
unit.
Each owner and operator is required
to use closed-vent systems to collect and
route natural gas emissions to the
respective VOC control devices. All vent
lines, connections, fittings, valves, relief
valves, or any other appurtenance
employed to contain and collect gases,
and transport them to the VOC control
equipment must be maintained and
operated properly during any time the
control equipment is operating and
must be designed to operate with no
detectable natural gas emissions. If a
closed-vent system contains one or more
bypass devices that could be used to
divert all or a portion of the natural gas
from entering the VOC control devices,
the owner or operator must meet one of
the following options for each bypass
device: (1) At the inlet to the bypass
device properly install, calibrate,
maintain, and operate a natural gas flow
indicator capable of taking periodic
readings and sounding an alarm when
the bypass device is open such that the
natural gas is being, or could be,
diverted away from the control device
and into the atmosphere; or (2) secure
the bypass device valve in the nondiverting position using a car-seal or a
lock-and-key type configuration.
Each owner or operator is required to
follow the manufacturer’s written
operating instructions, procedures and
maintenance schedule to ensure good
air pollution control practices for
minimizing emissions from each
enclosed combustor or utility flare. Each
enclosed combustor must have the
capacity to reduce the mass content of
the VOC in the natural gas routed to it
by at least 98.0% for the minimum and
maximum natural gas volumetric flow
rate and British Thermal Unit (BTU)
content routed to it. For the purposes of
this rule, we require that all utility flares
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17853
installed per this rule meet the
requirements in 40 CFR 60.18(b), and all
enclosed combustors installed per this
rule must be tested according to the
NSPS OOOO performance testing
requirements. Until such time that
compliance is required with the storage
vessel requirements in the NSPS OOOO
standard, however, the owner or
operators can demonstrate compliance
using methods specified in this rule.
We determined that certain work
practice and operational requirements
are also necessary for the practical
enforceability of the VOC emission
reduction requirement that the enclosed
combustors or utility flares must
achieve. Flares and combustors must be
operated within specific parameters to
effectively destroy VOC emissions.
Therefore, each owner or operator must
ensure that each enclosed combustor or
utility flare is: (1) Operated at all times
that produced natural gas and natural
gas emissions are routed to it; (2)
operated with a liquid knock-out system
to collect any condensable vapors (to
prevent liquids from going through the
control device); (3) equipped with a
flash-back flame arrestor; (4) equipped
with a continuous burning pilot flame
or an electronically controlled
electronically controlled automatic
igniter system; (5) equipped with a
monitoring system for continuous
recording of the parameters that indicate
proper operation of each enclosed
combustor, utility flare, continuous
burning pilot flame and electronically
controlled automatic igniter, such as a
chart recorder, data logger, or similar
devices; (6) maintained in a leak free
condition; and (7) operated with no
visible smoke emissions.
Section 49.4165 requires that each
owner or operator limit the use of pit
flares to: (1) The control natural gas
emissions during well completion
operations; (2) the control of VOC
emissions in the event the natural gas
that is being recovered for sale or other
beneficial purpose must be diverted to
a backup control device because
injection into the pipeline is
temporarily infeasible and there is no
operational enclosed combustor or
utility flare at the oil and natural gas
production facility, in which instances
the owner or operator must limit use of
the pit flare to no more than 500 hours
in any consecutive 12-month period; or
(3) use when total uncontrolled PTE of
VOCs from all produced oil storage
tanks and any produced water storage
tanks interconnected with produced oil
storage tanks at an oil and natural gas
production facility have declined to less
than, and are reasonably expected to
stay below, 20 tons in any consecutive
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12-month period. Each pit flare must be
operated to reduce the mass content of
VOC in the natural gas routed to it by
at least 90.0% and must be operated
with no visible smoke emissions. Each
pit flare must be equipped with an
electronically controlled automatic
igniter with malfunction alarm and
remote notification system if the pilot
flame fails. Each pit flare must be
visually inspected for the presence of a
pilot flame any time natural gas is being
routed to it and if the pilot flame fails,
it must be relit as soon as safely possible
and the electronically controlled
automatic igniter must be repaired or
replaced before the pit flare is used
again.
Section 49.4165 allows owners or
operators of oil and natural gas
production facilities to use control
devices other than an enclosed
combustor or utility flare, provided they
are capable of achieving at least a 98.0%
VOC destruction efficiency and upon
our prior written approval by the EPA.
This provision will allow for owner or
operators to take advantage of
technological advances in VOC
emission control for the oil and natural
gas production industry and will
provide us with valuable information on
any new control technologies.
Deletion: We have deleted the testing
requirement at § 49.4165(c)(5)(iii). This
was a temporary enclosed combustor
testing requirement that applied until 40
CFR part 60 subpart OOOO-New Source
Performance Standard for Oil and
Natural Gas Sector (NSPS OOOO) was
promulgated. Since NSPS OOOO was
promulgated on August 16, 2012 and
became effective on October 15, 2012,
this temporary provision is no longer
necessary.
Correction: We have clarified control
equipment requirements at
§ 49.4165(c)(4). We have added language
at § 49.4165(c)(4) to provide an
exemption to § 60.18(c)(2) and (f)(2) for
those utility flares operated with an
electronically controlled automatic
igniter as set forth in the regulatory text
of this final rule.
Clarification: We have clarified that
enclosed combustors and utility flares
must be operated properly at all times
that produced natural gas and/or natural
gas emissions are routed to them, rather
than just the term natural gas. The rule
now reads as set forth in the regulatory
text of this final rule at
§ 49.4165(c)(6)(i).
Correction: We have removed the
requirement to install equipment for the
monitoring of continuous burning pilot
flames and electronically controlled
automatic igniters on flares and
combustors. These requirements were
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already provided for at § 49.4166(g)(1).
The rule now reads as set forth in the
regulatory text of this final rule at
§ 49.4165(c)(6)(iv).
Clarification: We have clarified the
purpose for equipping utility flares and
enclosed combustors with a monitoring
system. We have revised the applicable
provisions to read as set forth in the
regulatory text of this final rule at
§ 49.4165(c)(6)(v).
Correction: We removed the
requirement to monitor a pilot flame on
pit flares since these flares are to be
operated with electronically controlled
automatic igniters only. The rule now
reads as set forth in the regulatory text
of this final rule at § 49.4165((d)(3(iv)
and (v).
G. Monitoring Requirements
Section 49.4166 Monitoring
Requirements requires each owner or
operator conduct certain monitoring
that we determined is necessary for the
practical enforceability of the VOC
emission reduction requirements,
including but not limited to: (1)
Monitoring of the number of barrels of
oil produced at the facility each time the
oil is unloaded from the produced oil
storage tanks; (2) Monitoring of the
hours of operation of each pit flare used
to control VOC emissions in the event
the natural gas that is being recovered
for sale or other beneficial purpose must
be diverted to a backup control device
because injection into the pipeline is
temporarily infeasible and there is no
operational enclosed combustor or
utility flare is at the oil and natural gas
production facility; (3) Monitoring of
the volume of produced natural gas
from the heater-treater sent to each
enclosed combustor, utility flare, and
pit flare at all times; (4) Monitoring of
the volume of standing, working,
breathing, and flashing losses from the
produced oil and produced water
storage tanks sent to each vapor
recovery system, enclosed combustor,
utility flare, and pit flare at all times; (5)
Visually inspecting storage tank thief
hatches, covers, seals, PRVs, and closedvent systems to insure proper condition
and functioning; (6) Directly and
continuously measuring, various
parameters (i.e., product throughput,
enclosed combustor flame presence,
temperature, etc.) related to the proper
operation of emissions units and
required control devices to assure
compliance with the emissions
reduction requirements and operational
limitations; and (7) Visually inspect all
equipment associated with each
enclosed combustor, utility flare, and
pit flare at a minimum quarterly to
ensure system integrity; (8) Visually
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monitoring for visible smoke from
enclosed combustors, utility flares, and
pit flares during operation.
The monitoring, recordkeeping and
reporting requirements for the covers,
close-vent systems, pit flares, enclosed
combustors, and utility flares are
intended to provide legal and
practicable enforceability of the
emission control requirements.
Correction: We have added
monitoring requirements at § 49.4166(d)
to describe acceptable gas volume
measurement methods, thus making this
provision consistent with the provision
at § 49.4166(c). The rule now reads as
set forth in the regulatory text of this
final rule.
Revision: We have included more
flexibility in the options for monitoring
approaches. We have revised the
applicable provisions to read as set forth
in the regulatory text of this final rule
at § 49.4166(g)(1).
Revision: We have clarified the intent
of the provision at § 49.4166(g)(2) in the
final FIP to read as set forth in the
regulatory text of this final rule:
Revision: We have revised the smoke
monitoring provisions at § 49.4166(g)(3)
in the final FIP to read as set forth in
the regulatory text of this final rule.
Revision: We have added a new
monitoring provision at § 49.4166(i) to
allow for other monitoring options upon
prior written approval by the EPA, as set
forth in the regulatory text of this final
rule.
H. Recordkeeping Requirements
Section 49.4167 Recordkeeping
Requirements requires that each owner
or operator of an oil and natural gas
production facility keep specific records
to be made available upon our request,
in lieu of voluminous reporting
requirements. The records that must be
kept include, but are not limited to, all
required measurements, monitoring,
and deviations or exceedances of rule
requirements and corrective actions
taken, as well as any manufacturer
specifications and guarantees or
engineering analyses. These
recordkeeping requirements provide
legal and practical enforceability to the
control and emission reduction
requirements of this rule.
Clarification: We have clarified the
recordkeeping requirements at
§ 49.4167(a)(4)(ii) to correctly identify
that casing head gas vented from
producing wells should be monitored,
not produced natural gas. The rule now
reads as set forth in the regulatory text
of this final rule.
Revision: We have revised the
recordkeeping requirements at
§ 49.4167(a)(8) to clarify that records
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must be maintained of the volume of
natural gas emissions released when
close-vent systems and control devices
have been bypassed or were not
operating. The rule now reads as set
forth in the regulatory text of this final
rule.
Correction: We have corrected the
recordkeeping requirements at
49.4167(a)(5)(iv) to include the
requirement to keep records of any
instance in which an electronically
controlled automatic igniter has failed.
The rule now reads as set forth in the
regulatory text of this final rule.
I. Reporting Requirements
Section 49.4168 Notification and
Reporting Requirements requires that
each owner or operator of an oil and
natural gas production facility prepare
and submit an annual report, beginning
one year after this rule becomes
effective covering the period for the
previous calendar year. The report must
include a summary of required records
identifying each oil and natural gas
production well completion or
recompletion operation for each facility
conducted during the reporting period,
an identification of the first date of
production for each oil and natural gas
production well at each facility that
commenced operation during the
reporting period, and a summary of
deviations or exceedances of any
requirements of this FIP and the
corrective measures taken. Additionally,
a report must be submitted for any
performance test we require.
Clarification: Upon further review of
the language at § 49.4168(b) regarding
annual reporting requirements, we
determined it was necessary to clarify
the requirement based on our original
intent. The provision now reads as set
forth in the regulatory text of this final
rule:
We decided not to require owners or
operators to register their oil and natural
gas production facilities, because the
Federal Tribal NSR Rule at 40 CFR
49.151 already requires registration of
existing minor sources and such a
requirement in this rule would be
redundant.
These reporting requirements are part
of providing legal and practical
enforceability to the control and
emission reduction requirements of this
rule.
Revision: As explained in the
response to comments above, we have
added a provision for notification and
reporting requirements at
§ 49.4168(b)(4)(iv) requiring owners or
operators to certify as to the truth,
accuracy and completeness of the
annual reports. The new provision is
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consistent with the NSPS OOOO (40
CFR 60.5420(b)(1)(iv)) and reads as set
forth in the regulatory text of this final
rule.
J. Effect on Permitting of Facilities
This rule is not a permitting program.
It does not impose or exempt the
facilities from any federal CAA
permitting requirements, including the
PSD preconstruction permitting
requirements at 40 CFR 52.21, Federal
Tribal NSR Rule permitting
requirements for minor sources at 40
CFR 49.151, or federal Title V operating
permit requirements at 40 CFR part 71.
The primary purpose of this rule is to
address potential impacts to the public
health and the environment. However,
the rule does provide legal and practical
enforceability for the use of VOC
emission controls that are already being
used voluntarily by the industry and for
VOC emissions reductions from those
controls. Provided that the facilities are
in compliance with the new rule, they
may take into account the enforceable
VOC emission reductions from the
required controls they use when
calculating their PTE for determining
applicability of the federal permitting
requirements, to the extent that the
effect those controls would have on
VOC emissions is legally and
practicably enforceable.
Regardless of this rule, due to the high
amount of associated natural gas in the
crude oil and the absence of
infrastructure to collect the natural gas
on the FBIR, some FBIR facilities’ PTE
of VOCs or any other pollutant subject
to regulation may exceed the
applicability thresholds for PSD,
Federal Tribal NSR Rule, or Title V
permitting even after accounting for the
legally and practicably enforceable
emission reductions provided in this
rule. In such cases, the owners or
operators of these facilities are required
to apply for and obtain the appropriate
permits in accordance with the
regulation.
K. Registration Requirements
This rule does not exempt facilities
located on the FBIR from the
registration requirements of the Federal
Tribal NSR Rule, promulgated on July 1,
2011. Nor does this rule impose any
additional registration requirements.
The primary purpose of this rule is to
address potential impacts to the public
health and the environment. Provided
that the facilities are in compliance with
the provisions of this rule, facilities may
include the enforceable VOC emission
reductions resulting from the controls
required in this rule when calculating
their PTE, to the extent that the effect
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those controls would have on VOC
emissions is legally and practicably
enforceable.
If the PTE VOCs or any other
regulated NSR pollutant is less than the
major source thresholds in 40 CFR
52.21, but equal to or greater than the
thresholds in the Federal Tribal NSR
Rule, then registration is required of
these facilities (40 CFR 49.160). Those
facilities that must obtain a PSD permit
pursuant to 40 CFR 52.21 or wish to
obtain a preconstruction permit
pursuant to 40 CFR 49.151 of the
Federal Tribal NSR Rule, in addition to
meeting the requirements of this rule,
are exempt from this registration
requirement.
VII. Statutory and Executive Order
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
This action is not a ‘‘significant
regulatory action’’ under the terms of
Executive Order 12866 (58 FR 51735,
October 4, 1993) and is therefore not
subject to review under Executive
Orders 12866 and 13563 (76 FR 3821,
January 21, 2011).
B. Paperwork Reduction Act
The information collection
requirements in this 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. An Information Collection
Request (ICR) document has been
prepared by us, and a copy is available
in the docket for this action. The
information collection requirements are
not enforceable until OMB approves
them. The ICR document prepared by us
has been assigned the EPA ICR tracking
number 2478.01.
The information requirements are
based on notification, recordkeeping
and reporting requirements in this FIP
(40 CFR part 49, subpart K). These
requirements are mandatory for each
owner or operator (1) Located on the
Fort Berthold Indian Reservation; (2)
constructing or operating an oil or
natural gas production facility
producing from the Bakken Pool with
one or more oil and natural gas wells
and (3) for which completion or
recompletion operations are/were
performed on or after August 12, 2007.
See 40 CFR 49.4161. These records and
reports are necessary for the EPA
Administrator (or the tribal agency if
delegated), for example, to: (1) Confirm
compliance status of stationary sources;
(2) identify any stationary sources not
subject to the requirements and identify
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stationary sources subject to the
regulations; and (3) ensure that the
stationary source control requirements
are being achieved. The information
would be used by the EPA or tribal
enforcement personnel to: (1) Indentify
stationary sources subject to the rules;
(2) ensure that appropriate control
technology is being properly applied;
and (3) ensure that the emission control
devices are being properly operated and
maintained on a continuous basis.
Based on the reported information, the
EPA Administrator (or the delegated
tribe) can decide which stationary
sources, records or processes should be
inspected.
Specifically, this FIP requires that
each owner or operator conduct certain
monitoring that we determined is
necessary for the practical enforceability
of the VOC emission reduction
requirements. See 40 CFR 49.4166. The
recordkeeping requirements in 40 CFR
49.4167 require that each owner or
operator keep specific records to be
made available at the EPA’s request. The
recordkeeping requirements require
only the specific information needed to
determine compliance. Finally, the rules
contain reporting requirements in 40
CFR 49.4168 that require each owner or
operator to prepare and submit an
annual report. These recordkeeping and
reporting requirements are specifically
authorized by CAA section 114 (42
U.S.C. 7414). We believe these
information collection requirements are
appropriate because they will enable us
to develop and maintain accurate
records of air pollution sources and
their emissions, will provide the
necessary legal and practical
enforceability, and will ensure
appropriate records are available to
verify compliance with this FIP. All
information submitted to us pursuant to
the recordkeeping and reporting
requirements for which a claim of
confidentiality is made is safeguarded
according to the Agency policies set
forth in 40 CFR part 2, subpart B.
It is estimated that 780 oil and natural
gas production facilities will be subject
to this FIP over the next three years. The
oil and natural gas production facilities
subject to this rule will incur
approximately 29,655 hours in annual
monitoring, reporting, and
recordkeeping burden (averaged over
the first three years after the effective
date of the rule), incurring an estimated
$6.5 million ($2012) in burden. This
includes an annual average of 29,655
labor hours per year at a total labor cost
of $1.4 million per year, average
annualized capital costs of $2.2 million
per year, average annual operating and
maintenance costs of $2.9 million per
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year, and an average annual estimate of
623 likely respondents over the next
three years. This estimate includes the
testing requirements, emission reports,
developing a monitoring plan,
notifications and recordkeeping. All
burden estimates are in 2012 calendar
year dollars and represent the most costeffective monitoring approach for
affected facilities. Burden is defined at
5 CFR 1320.3(b).
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 our regulations in 40 CFR
are listed in 40 CFR part 9. When this
ICR is approved by OMB, we 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 this final
rule.
To assist members of the public who
would like to provide comments on the
ICR, our need for this information, the
accuracy of the provided burden
estimates, and any suggested methods
for minimizing respondent burden, we
established a public docket for this rule,
which includes this ICR, under Docket
ID: EPA–R08–OAR–2012–0479. Submit
any comments related to the ICR to the
EPA and OMB. See ADDRESSES section
at the beginning of this notice for
information on submitting comments to
the EPA. 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 March 22,
2013, please attempt to send comments
to OMB by April 22, 2013. Before
finalizing the information collection
requirements, we will respond to any
comments submitted to the EPA or
OMB.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act (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 this rule on small entities, small
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entity is defined as: (1) A small business
as defined by the Small Business
Administration’s (SBA) 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.
After considering the economic
impacts of this final rule on small
entities, I certify that this action will not
have a significant economic impact on
a substantial number of small entities.
In determining whether a rule has a
significant economic impact on a
substantial number of small entities, the
impact of concern is any significant
adverse economic impact on small
entities, since the primary purpose of
the regulatory flexibility analyses is to
identify and address regulatory
alternatives ‘‘which minimize any
significant economic impact of the rule
on small entities’’ (5 U.S.C. 603 and
604). Thus, an agency may certify that
a rule will not have a significant
economic impact on a substantial
number of small entities if the rule
relieves regulatory burden, or otherwise
has a positive economic effect on all of
the small entities subject to the rule.
This rule will not have a significant
economic impact on a substantial
number of small entities due to the
reduced regulatory requirement, and
thus the regulatory burden, to obtain
federal CAA permits that this rule
provides.
D. Unfunded Mandates Reform Act
(UMRA)
This 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. As
discussed in the TSD and preamble for
the interim final rule, we determined
the maximum annual cost of
compliance with this rule on the oil and
natural gas industry is estimated to be
approximately $50 million. However,
we believe this is a conservative
estimate and that actual annual costs
would be much lower due to factors
such as increased facility well density,
standard industry practice to use VOC
control equipment, and anticipated
pipeline infrastructure development,
which is explained further in the TSD.
Thus, this rule is not subject to the
requirements of sections 202 or 205 of
UMRA.
This rule does not contain a
significant federal intergovernmental
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mandate as described by section 203 of
UMRA. Therefore, this 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.
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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 rule
regulates under the CAA certain
stationary sources in Indian country that
are not subject to approved CAA
programs of the State of North Dakota.
Thus, Executive Order 13132 does not
apply to this action. Although section 6
of Executive Order 13132 does not
apply to this action, we consulted with
the Three Affiliated Tribes of the
Mandan, Hidatsa, and Arikara Nation in
developing this action. A summary of
the consultation is provided below in
section F of this preamble. In the spirit
of Executive Order 13132, and
consistent with EPA policy to promote
communications between EPA and State
and local governments, EPA specifically
solicited comment on the 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’’ (65 FR
67249, November 6, 2000), requires us
to develop an accountable process to
ensure ‘‘meaningful and timely input by
tribal officials in the development of
regulatory policies that have tribal
implications.’’ ‘‘Policies that have tribal
implications’’ is defined in the
Executive Order to include regulations
that have ‘‘substantial direct effects on
one or more Indian tribes, on the
relationship between the Federal
Government and the Indian tribes, or on
the distribution of power and
responsibilities between the Federal
Government and Indian tribes.’’
Under Section 5(b) of Executive Order
13175, we may not issue a regulation
that has tribal implications, that
imposes substantial direct compliance
costs, and that is not required by statute,
unless the Federal Government provides
the funds necessary to pay the direct
compliance costs incurred by tribal
governments, or we consult with tribal
officials early in the process of
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developing the proposed regulation.
Under Section 5(c) of Executive Order
13175, we may not issue a regulation
that has tribal implications and that
preempts tribal law, unless the Agency
consults with tribal officials early in the
process of developing the proposed
regulation.
We concluded that this final rule will
have tribal implications. However, it
will neither impose substantial direct
compliance costs on tribal governments,
nor preempt tribal law. These
regulations would affect the FBIR
community by establishing air quality
regulations and thus creating a level of
air quality protection not previously
provided under the CAA. The regulatory
approach used in this rule would create
federal requirements similar to those
that are already in place areas adjacent
to the Reservation. Finally, although
tribal governments are encouraged to
partner with us on the implementation
of these regulations, they are not
required to do so. Since this final rule
will neither impose substantial direct
compliance costs on tribal governments,
nor preempt tribal law, the requirements
of Sections 5(b) and 5(c) of the
Executive Order do not apply to this
rule.
Consistent with EPA policy, the EPA
consulted with tribal officials and
representatives of the Three Affiliated
Tribes of the Mandan, Hidatsa and
Arikara Nation early in the process of
developing this regulation to permit
them to have meaningful and timely
input into its development.
Tribal consultation with the Three
Affiliated Tribes of the Mandan,
Hidatsa, and Arikara Nation was first
initiated on February 17, 2012 when we
mailed a letter inviting the Tribes to
consult on the first group of synthetic
minor NSR permits being issued on the
Reservation under the Federal Tribal
NSR Rule. Then, on March 29, 2012,
EPA senior management and the
Chairman of the Three Affiliated Tribes
of the Mandan, Hidatsa, and Arikara
Nation along with other government
officials met via conference call to
discuss the proposed FIP to be
developed for the FBIR. We formally
invited the Tribes to consult about this
FIP in a letter dated April 10, 2012 to
Chairman Tex Hall, of the Three
Affiliated Tribes of the Mandan,
Hidatsa, and Arikara Nation Council.
We again met with members of the
Three Affiliated Tribes of the Mandan,
Hidatsa, and Arikara Nation Council on
June 13, 2012 in New Town to consult
and receive input from the Tribes as we
developed this FIP. In attendance from
the Council were the vice Chairman and
two council members. The Tribes’ legal
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17857
counsel was also in attendance. The
purpose of the consultation was
twofold: (1) Update the Tribes on the
EPA’s efforts to develop this FIP so that
the air quality on the FBIR is protected
and oil and natural gas development
continues; and (2) discuss the Tribes’
preferences regarding involvement in
the FIP process. We provided
information on our plan to prepare a FIP
to ensure air quality protection while
preventing delays in oil and natural gas
production. We solicited the Tribes’
input on the FIP development. The
Council members present at the
consultation meeting indicated that they
strongly desired this FIP to be consistent
with North Dakota’s requirements for oil
and natural gas production facilities in
order to keep a level playing field for
development and continue
uninterrupted development of a key
economic resource for the Tribes. The
Council members expressed interest in
the future delegation of this FIP so that
the Tribes can implement the rule in
place of us. The Council members also
expressed interest in providing the
Tribes’ assistance in setting up a public
hearing for the rule.
As noted above, the Three Affiliated
Tribes of the Mandan, Hidatsa and
Arikara Nation have indicated
preliminary interest in seeking
administrative delegation of the Federal
Tribal NSR rule to assist us with
administration of that rule. We will
continue to work with the Three
Affiliated Tribes of the Mandan,
Hidatsa, and Arikara Nation if
administrative delegation is something
the Tribes decide to pursue.
Information containing the
consultation process is contained in the
docket for this rule.
For purposes of the final rule, we
specifically solicited additional
comments on the proposed action from
tribal officials. We did not receive any
comments on the proposed rule from
tribal officials during the public
comment period.
G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
The 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 action is not subject to
EO 13045 because the Agency does not
believe the environmental or safety risks
addressed by this action present a
disproportionate risk to children. In
addition, this rule requires control and
reduction of emissions of VOCs, which
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will have a beneficial effect on
children’s health by reducing air
pollution.
H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
This action is not subject to Executive
Order 13211 (66 FR 28355, May 22,
2001), because it is not a significant
regulatory action under Executive Order
12866.
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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, 12(d) (15 U.S.C. 272 note)
directs us 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 us to provide
Congress, through OMB, explanations
when the Agency decides not to use
available and applicable voluntary
consensus standards.
This rulemaking does not involve
technical standards. Therefore, we did
not consider the use of any voluntary
consensus standards.
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order 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.
We did a demographic analysis of the
areas closest to sources likely to be
covered by this rule, and found
disproportionately high concentrations
of minority and low income
populations. As detailed in our response
to comments, we took substantial steps
to ensure that such populations were
given the opportunity for meaningful
participation in the development of the
rule. In addition, we conducted an EJ
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analysis that determined that this rule
will not have disproportionately high
and adverse human health or
environmental effects of their programs,
policies, and activities on minority, lowincome, and indigenous populations,
because it ensures compliance with the
NAAQS, which provides environmental
and public health protection for all
affected populations, including
minority, low-income, and indigenous
populations.34
K. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. The EPA will
submit a report containing this rule and
other required information to the U.S.
Senate, the U.S. House of
Representatives and the Comptroller
General of the United States prior to
publication of the rule in the Federal
Register. A major rule cannot take effect
until 60 days after it is published in the
Federal Register. This action is not a
‘‘major rule’’ as defined by 5 U.S.C.
804(2). This rule will be effective 30
days from the date of publication, i.e.,
on April 22, 2013.
L. Judicial Review
Under section 307(b)(1) of the Act,
petitions for judicial review of this
action must be filed in the United States
Court of Appeals for the appropriate
circuit by May 21, 2013. Any such
judicial review is limited to only those
objections that are raised with
reasonable specificity in timely
comments. Filing a petition for
reconsideration by the Administrator of
this final rule does not affect the finality
of this rule for the purposes of judicial
review nor does it extend the time
within which a petition for judicial
review may be filed and shall not
postpone the effectiveness of such rule
or action. Under section 307(b)(2) of the
Act, the requirements of this final action
may not be challenged later in civil or
criminal proceedings brought by us to
enforce these requirements.
List of Subjects in 40 CFR Part 49
Environmental protection,
Administrative practice and procedure,
34 The TSD includes a more detailed explanation
of the EJ analysis for this FIP. It can be found in
the docket for this rule, Docket ID: EPA–R08–OAR–
2012–0479, which can be accessed at: https://
www.regulations.gov.
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Air pollution control, Indians,
Intergovernmental relations, Reporting
and recordkeeping requirements.
Dated: March 1, 2013.
Bob Perciasepe,
Acting Administrator.
40 CFR part 49 is amended as follows:
PART 49—[AMENDED]
1. The authority citation for part 49
continues to read as follows:
■
Authority: 42 U.S.C. 7401, et seq.
PART 49—INDIAN COUNTRY: AIR
QUALITY PLANNING AND
MANAGEMENT
Subpart K—Implementation Plans for
Tribes—Region VIII
2. Add §§ 49.4161 through 49.4168
and an undesignated center heading to
appear immediately before the newly
added § 49.4161 to read as follows:
*
*
*
*
*
■
Federal Implementation Plan for Oil
and Natural Gas Well Production
Facilities; Fort Berthold Indian
Reservation (Mandan, Hidatsa and
Arikara Nation), North Dakota
Sec.
Subpart
49.4161 Introduction.
49.4162 Delegation of authority of
administration to the tribes.
49.4163 General provisions.
49.4164 Construction and operational
control measures.
49.4165 Control equipment requirements.
49.4166 Monitoring requirements.
49.4167 Recordkeeping requirements.
49.4168 Notification and reporting
requirements.
*
*
*
*
*
Federal Implementation Plan for Oil
and Natural Gas Well Production
Facilities; Fort Berthold Indian
Reservation (Mandan, Hidatsa and
Arikara Nation), North Dakota
§ 49.4161
Introduction.
(a) What is the purpose of §§ 49.4161
through 49.4168? Sections 49.4161
through 49.4168 establish legally and
practicably enforceable requirements to
control and reduce VOC emissions from
well completion operations, well
recompletion operations, production
operations, and storage operations at
existing, new and modified oil and
natural gas production facilities.
(b) Am I subject to §§ 49.4161 through
49.4168? Sections 49.4161 through
49.4168 apply to each owner or operator
constructing, modifying or operating an
oil and natural gas production facility
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producing from the Bakken Pool with
one or more oil and natural gas wells,
for any one of which completion or
recompletion operations are/were
performed on or after August 12, 2007,
that is located on the Fort Berthold
Indian Reservation, which is defined by
the Act of March 3, 1891 (26 Statute
1032) and which includes all lands
added to the Reservation by Executive
Order of June 17, 1892 (the ‘‘Fort
Berthold Indian Reservation’’). For the
purposes of this subpart, the date that
the first well completion operation at a
new oil and natural gas production
facility was initiated is the date that
initial construction has commenced. For
the purposes of this subpart, the date
that a new well completion operation or
the date that an existing well
recompletion operation at an existing oil
and natural gas production facility is
initiated is the date that a modification
has commenced.
(c) When must I comply with
§§ 49.4161 through 49.4168?
Compliance with §§ 49.4161 through
49.4168 is required no later than June
20, 2013 or upon initiation of well
completion operations or well
recompletion operations, whichever is
later.
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§ 49.4162 Delegation of authority of
administration to the tribes.
(a) What is the purpose of this
section? The purpose of this section is
to establish the process by which the
Regional Administrator may delegate to
the Mandan, Hidatsa and Arikara Nation
the authority to assist the EPA with
administration of this Federal
Implementation Plan (FIP). This section
provides for administrative delegation
and does not affect the eligibility criteria
under 40 CFR 49.6 for treatment in the
same manner as a state.
(b) How does the Tribe request
delegation? In order to be delegated
authority to assist us with
administration of this FIP, the
authorized representative of the
Mandan, Hidatsa and Arikara Nation
must submit a request to the Regional
Administrator that:
(1) Identifies the specific provisions
for which delegation is requested;
(2) Includes a statement by the
Mandan, Hidatsa and Arikara Nation’s
legal counsel (or equivalent official) that
includes the following information:
(i) A statement that the Mandan,
Hidatsa and Arikara Nation are an
Indian Tribe recognized by the Secretary
of the Interior;
(ii) A descriptive statement
demonstrating that the Mandan, Hidatsa
and Arikara Nation are currently
carrying out substantial governmental
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duties and powers over a defined area
and that meets the requirements of
§ 49.7(a)(2); and
(iii) A description of the laws of the
Mandan, Hidatsa and Arikara Nation
that provide adequate authority to carry
out the aspects of the rule for which
delegation is requested.
(3) Demonstrates that the Mandan,
Hidatsa and Arikara Nation have, or will
have, adequate resources to carry out
the aspects of the rule for which
delegation is requested.
(c) How is the delegation of
administration accomplished? (1) A
Delegation of Authority Agreement will
set forth the terms and conditions of the
delegation, will specify the rule and
provisions that the Mandan, Hidatsa
and Arikara Nation shall be authorized
to implement on behalf of the EPA, and
shall be entered into by the Regional
Administrator and the Mandan, Hidatsa
and Arikara Nation. The Agreement will
become effective upon the date that both
the Regional Administrator and the
authorized representative of the
Mandan, Hidatsa and Arikara Nation
have signed the Agreement. Once the
delegation becomes effective, the
Mandan, Hidatsa and Arikara Nation
will be responsible, to the extent
specified in the Agreement, for assisting
us with administration of this FIP and
shall act as the Regional Administrator
as that term is used in these regulations.
Any Delegation of Authority Agreement
will clarify the circumstances in which
the term ‘‘Regional Administrator’’’
found throughout this FIP is to remain
the EPA Regional Administrator and
when it is intended to refer to the
‘‘Mandan, Hidatsa and Arikara Nation,’’
instead.
(2) A Delegation of Authority
Agreement may be modified, amended,
or revoked, in part or in whole, by the
Regional Administrator after
consultation with the Mandan, Hidatsa
and Arikara Nation.
(d) How will any delegation of
authority agreement be publicized? The
Regional Administrator shall publish a
notice in the Federal Register informing
the public of any delegation of authority
agreement with the Mandan, Hidatsa
and Arikara Nation to assist us with
administration of all or a portion of this
FIP and will identify such delegation in
the FIP. The Regional Administrator
shall also publish an announcement of
the delegation of authority agreement in
local newspapers.
§ 49.4163
General provisions.
(a) Definitions. As used in §§ 49.4161
through 49.4168, all terms not defined
herein shall have the meaning given
them in the Act, in subpart A and
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subpart OOOO of 40 CFR part 60, in the
Prevention of Significant Deterioration
regulations at 40 CFR 52.21, or in the
Federal Minor New Source Review
Program in Indian Country at 40 CFR
49.151. The following terms shall have
the specific meanings given them.
(1) Bakken Pool means Oil produced
from the Bakken, Three Forks, and
Sanish Formations.
(2) Breathing losses means natural gas
emissions from fixed roof tanks
resulting from evaporative losses during
storage.
(3) Casinghead natural gas means the
associated natural gas that naturally
dissolves out of reservoir fluids during
well completion operations and
recompletion operations due to the
pressure relief that occurs as the
reservoir fluids travel up the well
casinghead.
(4) Closed vent system means a system
that is not open to the atmosphere and
that is composed of hard-piping,
ductwork, connections, and, if
necessary, flow-inducing devices that
transport natural gas from a piece or
pieces of equipment to a control device
or back to a process.
(5) Enclosed combustor means a
thermal oxidation system with an
enclosed combustion chamber that
maintains a limited constant
temperature by controlling fuel and
combustion air.
(6) Existing facility means an oil and
natural gas production facility that
begins actual construction prior to the
effective date of the ‘‘Federal
Implementation Plan for Oil and Natural
Gas Well Production Facilities; Fort
Berthold Indian Reservation (Mandan,
Hidatsa and Arikara Nation), North
Dakota’’.
(7) Flashing losses means natural gas
emissions resulting from the presence of
dissolved natural gas in the produced
oil and the produced water, both of
which are under high pressure, that
occurs as the produced oil and
produced water is transferred to storage
tanks or other vessels that are at
atmospheric pressure.
(8) Modified facility means a facility
which has undergone the addition,
completion, or recompletion of one or
more oil and natural gas wells, and/or
the addition of any associated
equipment necessary for production and
storage operations at an existing facility.
(9) New facility means an oil and
natural gas production facility that
begins actual construction after the
effective date of the ‘‘Federal
Implementation Plan for Oil and Natural
Gas Well Production Facilities; Fort
Berthold Indian Reservation (Mandan,
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Hidatsa and Arikara Nation), North
Dakota’’.
(10) Oil means hydrocarbon liquids.
(11) Oil and natural gas production
facility means all of the air pollution
emitting units and activities located on
or integrally connected to one or more
oil and natural gas wells that are
necessary for production operations and
storage operations.
(12) Oil and natural gas well means a
single well that extracts subsurface
reservoir fluids containing a mixture of
oil, natural gas, and water.
(13) Owner or operator means any
person who owns, leases, operates,
controls, or supervises an oil and
natural gas production facility.
(14) Permit to construct or
construction permit means a permit
issued by the Regional Administrator
pursuant to 40 CFR 49.151, 52.10 or
52.21, or a permit issued by a tribe
pursuant to a program approved by the
Administrator under 40 CFR part 51,
subpart I, authorizing the construction
or modification of a stationary source.
(15) Permit to operate or operating
permit means a permit issued by the
Regional Administrator pursuant to 40
CFR part 71, or by a tribe pursuant to
a program approved by the
Administrator under 40 CFR part 51 or
40 CFR part 70, authorizing the
operation of a stationary source.
(16) Pit flare means an ignition
device, installed horizontally or
vertically and used in oil and natural
gas production operations to combust
produced natural gas and natural gas
emissions.
(17) Produced natural gas means
natural gas that is separated from
extracted reservoir fluids during
production operations.
(18) Produced oil means oil that is
separated from extracted reservoir fluids
during production operations.
(19) Produced oil storage tank means
a unit that is constructed primarily of
non-earthen materials (such as steel,
fiberglass, or plastic) which provides
structural support and is designed to
contain an accumulation of produced
oil.
(20) Produced water means water that
is separated from extracted reservoir
fluids during production operations.
(21) Produced water storage tank
means a unit that is constructed
primarily of non-earthen materials (such
as steel, fiberglass, or plastic) which
provides structural support and is
designed to contain an accumulation of
produced water.
(22) Production operations means the
extraction and separation of reservoir
fluids from an oil and natural gas well,
using separators and heater-treater
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systems. A separator is a pressurized
vessel designed to separate reservoir
fluids into their constituent components
of oil, natural gas and water. A heatertreater is a unit that heats the reservoir
fluid to break oil/water emulsions and
to reduce the oil viscosity. The water is
then typically removed by using gravity
to allow the water to separate from the
oil.
(23) Regional Administrator means
the Regional Administrator of EPA
Region 8 or an authorized representative
of the Regional Administrator.
(24) Standing losses means natural gas
emissions from fixed roof tanks as a
result of evaporative losses during
storage.
(25) Storage operations means the
transfer of produced oil and produced
water to storage tanks, the filling of the
storage tanks, the storage of the
produced oil and produced water in the
storage tanks, and the draining of the
produced oil and produced water from
the storage tanks.
(26) Supervisory Control and Data
Acquisition (SCADA) system generally
refers to industrial control computer
systems that monitor and control
industrial infrastructure or facilitybased processes.
(27) Utility flare means thermal
oxidation system using an open
(without enclosure) flame. An enclosed
combustor as defined in §§ 49.4161
through 49.4168 is not considered a
flare.
(28) Visible Smoke emissions means a
pollutant generated by thermal
oxidation in a flare or enclosed
combustor and occurring immediately
downstream of the flame. Visible smoke
occurring within, but not downstream
of, the flame, is not considered to
constitute visible smoke emissions.
(29) Well completion means the
process that allows for the flowback of
oil and natural gas from newly drilled
wells to expel drilling and reservoir
fluids and tests the reservoir flow
characteristics, which may vent
produced hydrocarbons to the
atmosphere via an open pit or tank.
(30) Well completion operation means
any oil and natural gas well completion
using hydraulic fracturing occurring at
an oil and natural gas production
facility.
(31) Well recompletion operation
means any oil and natural gas well
completion using hydraulic refracturing
occurring at an oil and natural gas
production facility.
(32) Working losses means natural gas
emissions from fixed roof tanks
resulting from evaporative losses during
filling and emptying operations.
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(b) Requirement for testing. The
Regional Administrator may require that
an owner or operator of an oil and
natural gas production facility
demonstrate compliance with the
requirements of the ‘‘Federal
Implementation Plan for Oil and Natural
Gas Well Production Facilities; Fort
Berthold Indian Reservation (Mandan,
Hidatsa and Arikara Nation), North
Dakota’’ by performing a source test and
submitting the test results to the
Regional Administrator. Nothing in the
‘‘Federal Implementation Plan for Oil
and Natural Gas Well Production
Facilities; Fort Berthold Indian
Reservation (Mandan, Hidatsa and
Arikara Nation), North Dakota’’ limits
the authority of the Regional
Administrator to require, in an
information request pursuant to section
114 of the Act, an owner or operator of
an oil and natural gas production
facility subject to the ‘‘Federal
Implementation Plan for Oil and Natural
Gas Production Facilities, Fort Berthold
Indian Reservation (Mandan, Hidatsa
and Arikara Nation)’’ to demonstrate
compliance by performing testing, even
where the facility does not have a
permit to construct or a permit to
operate.
(c) Requirement for monitoring,
recordkeeping, and reporting. Nothing
in ‘‘Federal Implementation Plan for Oil
and Natural Gas Production Facilities,
Fort Berthold Indian Reservation
(Mandan, Hidatsa and Arikara Nation)’’
precludes the Regional Administrator
from requiring monitoring,
recordkeeping and reporting, including
monitoring, recordkeeping and
reporting in addition to that already
required by an applicable requirement
in these rules, in a permit to construct
or permit to operate in order to ensure
compliance.
(d) Credible evidence. For the
purposes of submitting reports or
establishing whether or not an owner or
operator of an oil and natural gas
production facility has violated or is in
violation of any requirement, nothing in
the ‘‘Federal Implementation Plan for
Oil and Natural Gas Well Production
Facilities; Fort Berthold Indian
Reservation (Mandan, Hidatsa and
Arikara Nation), North Dakota’’ shall
preclude the use, including the
exclusive use, of any credible evidence
or information, relevant to whether a
facility would have been in compliance
with applicable requirements if the
appropriate performance or compliance
test had been performed.
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§ 49.4164 Construction and operational
control measures.
(a) Each owner or operator must
operate and maintain all liquid and gas
collection, storage, processing and
handling operations, regardless of size,
so as to minimize leakage of natural gas
emissions to the atmosphere.
(b) During all oil and natural gas well
completion operations or recompletion
operations at an oil and natural gas
production facility and prior to the first
date of production of each oil and
natural gas well, each owner or operator
must, at a minimum, route all
casinghead natural gas to a utility flare
or a pit flare capable of reducing the
mass content of VOC in the natural gas
emissions vented to it by at least 90.0
percent or greater and operated as
specified in §§ 49.4165 and 49.4166.
(c) Beginning with the first date of
production from any one oil and natural
gas well at an oil and natural gas
production facility, each owner or
operator must, at a minimum, route all
natural gas emissions from production
operations and storage operations to a
control device capable of reducing the
mass content of VOC in the natural gas
emissions vented to it by at least 90.0
percent or greater and operated as
specified in §§ 49.4165 and 49.4166.
(d) Within ninety (90) days of the first
date of production from any oil and
natural gas well at an oil and natural gas
production facility, each owner or
operator must:
(1) Route the produced natural gas
from the production operations through
a closed-vent system to:
(i) An operating system designed to
recover and inject all the produced
natural gas into a natural gas gathering
pipeline system for sale or other
beneficial purpose; or
(ii) A utility flare or equivalent
combustion device capable of reducing
the mass content of VOC in the
produced natural gas vented to the
device by at least 98.0 percent or greater
and operated as specified in §§ 49.4165
and 49.4166.
(2) Route all standing, working,
breathing, and flashing losses from the
produced oil storage tanks and any
produced water storage tank
interconnected with the produced oil
storage tanks through a closed-vent
system to:
(i) An operating system designed to
recover and inject the natural gas
emissions into a natural gas gathering
pipeline system for sale or other
beneficial purpose; or
(ii) An enclosed combustor or utility
flare capable of reducing the mass
content of VOC in the natural gas
emissions vented to the device by at
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least 98.0 percent or greater and
operated as specified in §§ 49.4165(c)
and 49.4166.
(iii) If the uncontrolled potential to
emit VOCs from the aggregate of all
produced oil storage tanks and
produced water storage tanks
interconnected with produced oil
storage tanks at an oil and natural gas
production facility is less than, and
reasonably expected to remain below,
20 tons in any consecutive 12-month
period, then, upon prior written
approval by the EPA the owner or
operator may use a pit flare, an enclosed
combustor or a utility flare that is
capable of reducing the mass content of
VOC in the natural gas emissions from
the storage tanks vented to the device by
only 90.0 percent.
(e) In the event that pipeline injection
of all or part of the natural gas collected
in an operating system designed to
recover and inject natural gas becomes
temporarily infeasible and there is no
operational enclosed combustor or
utility flare at the facility, the owner or
operator must route the natural gas that
cannot be injected through a closed-vent
system to a pit flare operated as
specified in §§ 49.4165 and 49.4166.
(f) Produced oil storage tanks and any
produced water storage tanks
interconnected with produced oil
storage tanks subject to the requirements
specified in 40 CFR part 60, subpart
OOOO are considered to meet the
requirements of § 49.4164(d)(2). No
further requirements apply for such
storage tanks under § 49.4164(d)(2).
§ 49.4165 Control equipment
requirements.
(a) Covers. Each owner or operator
must equip all openings on each
produced oil storage tank and produced
water storage tank interconnected with
produced oil storage tanks with a cover
to ensure that all natural gas emissions
are efficiently being routed through a
closed-vent system to a vapor recovery
system, an enclosed combustor, a utility
flare, or a pit flare.
(1) Each cover and all openings on the
cover (e.g., access hatches, sampling
ports, pressure relief valves (PRV), and
gauge wells) shall form a continuous
impermeable barrier over the entire
surface area of the produced oil and
produced water in the storage tank.
(2) Each cover opening shall be
secured in a closed, sealed position
(e.g., covered by a gasketed lid or cap)
whenever material is in the unit on
which the cover is installed except
during those times when it is necessary
to use an opening as follows:
(i) To add material to, or remove
material from the unit (this includes
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openings necessary to equalize or
balance the internal pressure of the unit
following changes in the level of the
material in the unit);
(ii) To inspect or sample the material
in the unit; or
(iii) To inspect, maintain, repair, or
replace equipment located inside the
unit.
(3) Each thief hatch cover shall be
weighted and properly seated.
(4) Each PRV shall be set to release at
a pressure that will ensure that natural
gas emissions are routed through the
closed-vent system to the vapor
recovery system, the enclosed
combustor, or the utility flare under
normal operating conditions.
(b) Closed-vent systems. Each owner
or operator must meet the following
requirements for closed-vent systems:
(1) Each closed-vent system must
route all produced natural gas and
natural gas emissions from production
and storage operations to the natural gas
sales pipeline or the control devices
required by paragraph (a) of this section.
(2) All vent lines, connections,
fittings, valves, relief valves, or any
other appurtenance employed to contain
and collect natural gas, vapor, and
fumes and transport them to a natural
gas sales pipeline and any VOC control
equipment must be maintained and
operated properly at all times.
(3) Each closed-vent system must be
designed to operate with no detectable
natural gas emissions.
(4) If any closed-vent system contains
one or more bypass devices, except as
provided for in paragraph (b)(4)(iii) of
this section, that could be used to divert
all or a portion of the natural gas
emissions, from entering a natural gas
sales pipeline and/or any control
devices, the owner or operator must
meet the one of following requirements
for each bypass device:
(i) At the inlet to the bypass device
that could divert the natural gas
emissions away from a natural gas sales
pipeline or a control device and into the
atmosphere, properly install, calibrate,
maintain, and operate a natural gas flow
indicator that is capable of taking
continuous readings and sounding an
alarm when the bypass device is open
such that natural gas emissions are
being, or could be, diverted away from
a natural gas sales pipeline or a control
device and into the atmosphere;
(ii) Secure the bypass device valve
installed at the inlet to the bypass
device in the non-diverting position
using a car-seal or a lock-and-key type
configuration;
(iii) Low leg drains, high point bleeds,
analyzer vents, open-ended valves or
lines, and safety devices are not subject
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to the requirements applicable to bypass
devices.
(c) Enclosed combustors and utility
flares. Each owner or operator must
meet the following requirements for
enclosed combustors and utility flares:
(1) For each enclosed combustor or
utility flare, the owner or operator must
follow the manufacturer’s written
operating instructions, procedures and
maintenance schedule to ensure good
air pollution control practices for
minimizing emissions;
(2) For each enclosed combustor or
utility flare, the owner or operator must
ensure there is sufficient capacity to
reduce the mass content of VOC in the
produced natural gas and natural gas
emissions routed to it by at least 98.0
percent for the minimum and maximum
natural gas volumetric flow rate and
BTU content routed to the device;
(3) Each enclosed combustor or utility
flare must be operated to reduce the
mass content of VOC in the produced
natural gas and natural gas emissions
routed to it by at least 98.0 percent;
(4) The owner or operator must ensure
that each utility flare is designed and
operated in accordance with the
requirements of 40 CFR 60.18(b) for
such flares, except for § 60.18(c)(2) and
(f)(2) for those utility flares operated
with an electronically controlled
automatic igniter.
(5) The owner or operator must ensure
that each enclosed combustor is:
(i) A model demonstrated by a
manufacturer to the meet the VOC
destruction efficiency requirements of
§§ 49.4161 through 49.4168 using the
procedure specified in 40 CFR part 60,
subpart OOOO at § 60.5413(d) by the
due date of the first annual report as
specified in § 49.4168(b); or
(ii) Demonstrated to meet the VOC
destruction efficiency requirements of
§§ 49.4161 through 49.4168 using EPA
approved performance test methods
specified in 40 CFR part 60, subpart
OOOO at § 60.5413(b) by the due date
of the first annual report as specified in
§ 49.4168(b).
(6) The owner or operator must ensure
that each enclosed combustor and
utility flare is:
(i) Operated properly at all times that
produced natural gas and/or natural gas
emissions are routed to it;
(ii) Operated with a liquid knock-out
system to collect any condensable
vapors (to prevent liquids from going
through the control device);
(iii) Equipped with a flash-back flame
arrestor;
(iv) Equipped with one of the
following:
(A) A continuous burning pilot flame.
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(B) An electronically controlled
automatic igniter;
(v) Equipped with a monitoring
system for continuous recording of the
parameters that indicate proper
operation of each enclosed combustor,
utility flare, continuous burning pilot
flame, and electronically controlled
automatic igniter, such as a chart
recorder, data logger or similar devices;
(vi) Maintained in a leak-free
condition; and
(vii) Operated with no visible smoke
emissions.
(d) Pit Flares. Each owner or operator
must meet the following requirements
for pit flares:
(1) The owner or operator must
develop written operating instructions,
operating procedures and maintenance
schedules to ensure good air pollution
control practices for minimizing
emissions from the pit flare based on the
site-specific design.
(2) The owner or operator must only
use a pit flare for the following
operations:
(i) To control produced natural gas
and natural gas emissions during well
completion operations or recompletion
operations;
(ii) To control produced natural gas
and natural gas emissions in the event
that natural gas recovered for pipeline
injection must be diverted to a backup
control device because injection is
temporarily infeasible and there is no
operational enclosed combustor or
utility flare at the oil and natural gas
production facility. Use of the pit flare
for this situation is limited to a
maximum of 500 hours in any twelve
(12) consecutive months; or
(iii) Control of standing, working,
breathing, and flashing losses from the
produced oil storage tanks and any
produced water storage tank
interconnected with the produced oil
storage tanks if the uncontrolled
potential VOC emissions from the
aggregate of all produced oil storage
tanks and produced water storage tanks
interconnected with produced oil
storage tanks is less than, and
reasonably expected to remain below,
20 tons in any consecutive 12-month
period.
(3) The owner or operator must only
use the pit flare under the following
conditions and limitations:
(i) The pit flare is operated to reduce
the mass content of VOC in the
produced natural gas and natural gas
emissions routed to it by at least 90.0
percent;
(ii) The pit flare is operated in
accordance with the site-specific written
operating instructions, operating
procedures, and maintenance schedules
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to ensure good air pollution control
practices for minimizing emissions;
(iii) The pit flare is operated with no
visible smoke emissions;
(iv) The pit flare is equipped with an
electronically controlled automatic
igniter;
(v) The pit flare is visually inspected
for the presence of a flame anytime
produced natural gas or natural gas
emissions are being routed to it. Should
the flame fail, the flame must be relit as
soon as safely possible and the
electronically controlled automatic
igniter must be repaired or replaced
before the pit flare is utilized again; and
(vi) The owner or operator does not
deposit or cause to be deposited into a
flare pit any oil field fluids or oil and
natural gas wastes other than those
designed to go to the pit flare.
(e) Other Control Devices. Upon prior
written approval by the EPA, the owner
or operator may use control devices
other than those listed above that are
determined by EPA to be capable of
reducing the mass content of VOC in the
natural gas routed to it by at least 98.0
percent, provided that:
(1) In operating such control devices,
the owner or operator must follow the
manufacturer’s written operating
instructions, procedures and
maintenance schedule to ensure good
air pollution control practices for
minimizing emissions; and
(2) The owner or operator must ensure
there is sufficient capacity to reduce the
mass content of VOC in the produced
natural gas and natural gas emissions
routed to such other control devices by
at least 98.0 percent for the minimum
and maximum natural gas volumetric
flow rate and BTU content routed to
each device.
(3) The owner or operator must
operate such a control device to reduce
the mass content of VOC in the
produced natural gas and natural gas
emissions routed to it by at least 98.0
percent.
§ 49.4166
Monitoring requirements.
(a) Each owner and operator must
measure the barrels of oil produced at
the oil and natural gas production
facility each time the oil is unloaded
from the produced oil storage tanks
using the methodologies of tank gauging
or positive displacement metering
system, as appropriate, as established by
the U.S. Department of the Interior’s
Bureau of Land Management at 43 CFR
part 3160, in the ‘‘Onshore Oil and Gas
Operations; Federal and Indian Oil &
Gas Leases; Onshore Oil and Gas Order
No. 4; Measurement of Oil’’.
(b) Each owner or operator must
monitor the hours that each pit flare is
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operated to control produced natural gas
and natural gas emissions in the event
that natural gas recovered for pipeline
injection must be diverted to a backup
control device because injection is
temporarily infeasible and there is no
enclosed combustor or utility flare at the
oil and natural gas production facility.
(c) Each owner or operator must
monitor the volume of produced natural
gas sent to each enclosed combustor,
utility flare, and pit flare at all times.
Methods to measure the volume
include, but are not limited to, direct
measurement and gas-to-oil ratio (GOR)
laboratory analyses.
(d) Each owner or operator must
monitor the volume of standing,
working, breathing, and flashing losses
from the produced oil and produced
water storage tanks sent to each vapor
recovery system, enclosed combustor,
utility flare, and pit flare at all times.
Methods to measure the volume
include, but are not limited to, direct
measurement or GOR laboratory
analyses.
(e) Each owner or operator must
perform quarterly visual inspections of
tank thief hatches, covers, seals, PRVs,
and closed vent systems to ensure
proper condition and functioning and
repair any damaged equipment. The
quarterly inspections must be performed
while the produced oil and produced
water storage tanks are being filled.
(f) Each owner or operator must
perform quarterly visual inspections of
the peak pressure and vacuum values in
each closed vent system and control
system for the produced oil and
produced water storage tanks to ensure
that the pressure and vacuum relief setpoints are not being exceeded in a way
that has resulted, or may result, in
venting and possible damage to
equipment. The quarterly inspections
must be performed while the produced
oil and produced water storage tanks are
being filled.
(g) Each owner or operator must
monitor the operation of each enclosed
combustor, utility flare, and pit flare to
confirm proper operation as follows:
(1) Continuously monitor all variable
operational parameters specified in the
written operating instructions and
procedures, including continuous
burning pilot flame, electronically
controlled automatic igniters, and
monitoring system failures, using a
malfunction alarm and remote
notification system, where such systems
are available, or continuously monitor
under an equivalent alternative protocol
upon prior written approval by the EPA;
(2) Perform a physical inspection of
all equipment associated with each
enclosed combustor, utility flare, and
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pit flare each time an operator is on site,
at a minimum quarterly, to ensure
system integrity;
(3) Monitor for visible smoke during
operation of any enclosed combustor,
utility flare or pit flare each time an
operator is on site, at a minimum
quarterly. Upon observation of visible
smoke, use EPA Reference Method 22 of
40 CFR part 60, Appendix A, to
determine whether visible smoke
emissions are present. The observation
period shall be 2 hours. Visible smoke
emissions are present if smoke is
observed for more than 5 minutes in any
2 consecutive hours; and
(4) Respond to any observation of any
continuous burning pilot flame failure,
electronically controlled automatic
igniter failure, or improper monitoring
equipment operation and ensure the
equipment is returned to proper
operation as soon as practicable and
safely possible after an observation or an
alarm sounds.
(h) Where sufficient to meet the
monitoring and recordkeeping
requirements in §§ 49.4166 and 49.4167,
the owner or operator may use a
Supervisory Control and Data
Acquisition (SCADA) system to monitor
and record the required data in
§§ 49.4161 through 49.4168.
(i) Other Monitoring Options. The
owner or operator may use equivalent
methods of monitoring other than those
listed above upon prior written approval
by the EPA.
§ 49.4167
Recordkeeping requirements.
(a) Each owner or operator must
maintain the following records:
(1) The measured barrels of oil
produced at the oil and natural gas
production facility each time the oil is
unloaded from the produced oil storage
tanks;
(2) The volume of produced natural
gas sent to each enclosed combustor,
utility flare, and pit flare at all times;
(3) The volume of natural gas
emissions from the produced oil storage
tanks and produced water storage tanks
sent to each enclosed combustor, utility
flare, and pit flare at all times;
(4) A summary of each oil and natural
gas well completion operation and
recompletion operation at an oil and
natural gas production facility. Each
summary shall include:
(i) The latitude and longitude location
of the oil and natural gas well in
decimal format;
(ii) The date, time, and duration in
hours of flowback from the oil and
natural gas well;
(iii) The date, time, and duration in
hours of any venting of casinghead
PO 00000
Frm 00029
Fmt 4701
Sfmt 4700
17863
natural gas from the oil and natural gas
well; and
(iv) Specific reasons for each instance
of venting in lieu of capture or
combustion.
(5) For each enclosed combustor,
utility flare, and pit flare at an oil and
natural gas production facility:
(i) Written, site-specific designs,
operating instructions, operating
procedures and maintenance schedules;
(ii) Records of all required monitoring
of operations;
(iii) Records of any deviations from
the operating parameters specified by
the written site-specific designs,
operating instructions, and operating
procedures. The records must include
the enclosed combustor, utility flare, or
pit flare’s total operating time during
which a deviation occurred, the date,
time and length of time that deviations
occurred, and the corrective actions
taken and any preventative measures
adopted to operate the device within
that operating parameter;
(iv) Records of any instances in which
the pilot flame is not present,
electronically controlled automatic
igniter is not functioning, or the
monitoring equipment is not
functioning in the enclosed combustor,
the utility flare, or the pit flare, the date
and times of the occurrence, the
corrective actions taken, and any
preventative measures adopted to
prevent recurrence of the occurrence;
(v) Records of any instances in which
a recording device installed to record
data from the enclosed combustor,
utility flare, or pit flare is not
operational; and
(vi) Records of any time periods in
which visible smoke emissions are
observed emanating from the enclosed
combustor, utility flare, or pit flare.
(6) For each pit flare at an oil and
natural gas production facility, a
demonstration of compliance with the
use restrictions set forth in
§ 49.4165(d)(2)(ii) is made by keeping
records in a log book, or similar
recording system, during each period of
time that the pit flare is operating. The
records must contain the following
information:
(i) Date and time the pit flare was
started up and subsequently shut down;
(ii) Total hours operated when
pipeline injection was temporarily
infeasible for the current calendar
month plus the previous consecutive
eleven (11) calendar months; and
(iii) Brief descriptions of the
justification for each period of
operation.
(7) Records of any instances in which
any closed-vent system or control
device was bypassed or down, the
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Federal Register / Vol. 78, No. 56 / Friday, March 22, 2013 / Rules and Regulations
reason for each incident, its duration,
the volume of natural gas emissions
released, and the corrective actions
taken and any preventative measures
adopted to avoid such bypasses or
downtimes; and
(8) Documentation of all produced oil
storage tank and produced water storage
tank inspections required in
§ 49.4166(e) and (f). All inspection
records must include, at a minimum,
the following information:
(i) The date of the inspection;
(ii) The findings of the inspection;
(iii) Any adjustments or repairs made
as a result of the inspections, and the
date of the adjustment or repair; and
(iv) The inspector’s name and
signature.
(b) Each owner or operator must keep
all records required by this section
onsite at the facility or at the location
that has day-to-day operational control
over the facility and must make the
records available to the EPA upon
request.
(c) Each owner or operator must retain
all records required by this section for
a period of at least five (5) years from
the date the record was created.
§ 49.4168 Notification and reporting
requirements.
mstockstill on DSK4VPTVN1PROD with RULES2
(a) Each owner or operator must
submit any documents required under
this section to: U.S. Environmental
Protection Agency, Region 8 Office of
VerDate Mar<15>2010
18:39 Mar 21, 2013
Jkt 229001
Enforcement, Compliance &
Environmental Justice, Air Toxics and
Technical Enforcement Program, 8ENF–
AT, 1595 Wynkoop Street, Denver,
Colorado 80202. Documents may be
submitted electronically to
r8airreportenforcement@epa.gov.
(b) Each owner and operator must
submit an annual report containing the
information specified in paragraphs
(b)(1) through (4) of this section. Each
annual report is due August 15th every
year and must cover all information for
the previous calendar year. The initial
report must cover the cumulative
information for that year. If you own or
operate more than one oil and natural
gas production facility, you may submit
one report for multiple oil and natural
gas production facilities provided the
report contains all of the information
required as specified in paragraphs
(b)(1) through (4) of this section. Annual
reports may coincide with title V reports
as long as all the required elements of
the annual report are included. The EPA
may approve a common schedule on
which reports required by §§ 49.4161
through 49.4168 may be submitted as
long as the schedule does not extend the
reporting period.
(1) The company name and the
address of the oil and natural gas
production facility or facilities.
(2) An identification of each oil and
natural gas production facility being
included in the annual report.
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Frm 00030
Fmt 4701
Sfmt 9990
(3) The beginning and ending dates of
the reporting period.
(4) For each oil and natural gas
production facility, the information in
paragraphs (b)(4)(i) through (iv) of this
section.
(i) A summary of all required records
identifying each oil and natural gas well
completion or recompletion operation
for each oil and natural gas production
facility conducted during the reporting
period;
(ii) An identification of the first date
of production for each oil and natural
gas well at each oil and natural gas
production facility that commenced
production during the reporting period;
and
(iii) A summary of cases where
construction or operation was not
performed in compliance with the
requirements specified in § 49.4164,
§ 49.4165, or § 49.4166 for each oil and
natural gas well at each oil and natural
gas production facility, and the
corrective measures taken.
(iv) A certification by a responsible
official of truth, accuracy and
completeness. This certification shall
state that, based on information and
belief formed after reasonable inquiry,
the statements and information in the
document are true, accurate and
complete.
[FR Doc. 2013–05666 Filed 3–21–13; 8:45 am]
BILLING CODE 6560–50–P
E:\FR\FM\22MRR2.SGM
22MRR2
Agencies
[Federal Register Volume 78, Number 56 (Friday, March 22, 2013)]
[Rules and Regulations]
[Pages 17835-17864]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2013-05666]
[[Page 17835]]
Vol. 78
Friday,
No. 56
March 22, 2013
Part III
Environmental Protection Agency
-----------------------------------------------------------------------
40 CFR Part 49
Approval and Promulgation of Federal Implementation Plan for Oil and
Natural Gas Well Production Facilities; Fort Berthold Indian
Reservation (Mandan, Hidatsa, and Arikara Nation), North Dakota; Rule
Federal Register / Vol. 78 , No. 56 / Friday, March 22, 2013 / Rules
and Regulations
[[Page 17836]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 49
[EPA-R08-OAR-2012-0479; FRL-9789-3]
Approval and Promulgation of Federal Implementation Plan for Oil
and Natural Gas Well Production Facilities; Fort Berthold Indian
Reservation (Mandan, Hidatsa, and Arikara Nation), North Dakota
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: The EPA is taking final action to promulgate a Reservation-
specific Federal Implementation Plan in order to regulate emissions
from oil and natural gas production facilities located on the Fort
Berthold Indian Reservation in North Dakota. The Federal Implementation
Plan includes basic air quality regulations for the protection of
communities in and adjacent to the Fort Berthold Indian Reservation.
The Federal Implementation Plan requires owners and operators of oil
and natural gas production facilities to reduce emissions of volatile
organic compounds emanating from well completions, recompletions, and
production and storage operations. This Federal Implementation Plan
will be implemented by the EPA, or a delegated tribal authority, until
replaced by a Tribal Implementation Plan. The EPA proposed a
Reservation-specific Federal Implementation Plan concurrently with an
interim final rule on August 15, 2012. This final Federal
Implementation Plan replaces the interim final rule in all intents and
purposes on the effective date of the final rule. The EPA is taking
this action pursuant to the Clean Air Act (CAA).
DATES: This final rule is effective on April 22, 2013.
ADDRESSES: The EPA has established a docket for this action under
Docket ID No. EPA-R08-OAR-2012-0479. All documents in the docket are
listed on the www.regulations.gov Web site. Although listed in the
index, some information is not publicly available, i.e., CBI or other
information whose disclosure is restricted by statute. Certain other
material, such as copyrighted material, is not placed on the Internet
and will be publicly available only in hard copy form. Publicly
available docket materials are available either electronically through
www.regulations.gov, or in hard copy at the Air Program, Environmental
Protection Agency (EPA), Region 8, 1595 Wynkoop Street, Denver,
Colorado 80202-1129. The EPA requests that if at all possible, you
contact the individual listed in the FOR FURTHER INFORMATION CONTACT
section to view the hard copy of the docket. You may view the hard copy
of the docket Monday through Friday, 8 a.m. to 4 p.m., excluding
federal holidays.
FOR FURTHER INFORMATION CONTACT: Deirdre Rothery, U.S. Environmental
Protection Agency, Region 8, Air Program, Mail Code 8P-AR, 1595 Wynkoop
Street, Denver, Colorado 80202-1129, (303) 312-6431,
rothery.deirdre@epa.gov.
SUPPLEMENTARY INFORMATION: Throughout this document, ``we'', ``us'',
and ``our'' refer to the EPA.
Definitions
For the purpose of this document, we are giving meaning to
certain words or initials as follows:
i. The initials APA mean or refer to the Administrative Procedure
Act.
ii. The words or initials Act or CAA mean or refer to the Clean Air
Act, unless the context indicates otherwise.
iii. The initials BTU mean or refer to British Thermal Unit.
iv. The initials CAFOs mean or refer to Consent Agreement Final
Orders.
v. The initials CDPHE mean or refer to Colorado Department of Public
Health and Environment Air Pollution Control Division.
vi. The initials CO mean or refer to carbon monoxide.
vii. The words EPA, we, us or our mean or refer to the United States
Environmental Protection Agency.
viii. The words Reservation or the initials FBIR mean or refer to
the Fort Berthold Indian Reservation.
ix. The initials FIP mean or refer to Federal Implementation Plan.
x. The initials GOR mean or refer to gas-to-oil ratio.
xi. The initials LACT mean or refer to lease automatic custody
transfer.
xii. The initials MDEQ mean or refer to Montana Department of
Environmental Quality.
xiii. The initials NAAQS mean or refer to the National Ambient Air
Quality Standards.
xiv. The initials NAICS mean or refer to the North American Industry
Classification System.
xv. The initials NDDoH mean or refer to the North Dakota Department
of Health.
xvi. The initials NDIC mean or refer to the North Dakota Industrial
Commission.
xvii. The initials NESHAP mean or refer to National Emission
Standards for Hazardous Air Pollutants.
xviii. The initials NMED mean or refer to New Mexico Environment
Department Air Quality Bureau.
xix. The initials NOX mean or refer to nitrogen oxides.
xx. The initials NO2 mean or refer to nitrogen dioxide.
xxi. The initials NSPS mean or refer to New Source Performance
Standards.
xxii. The initials NSR mean or refer to new source review.
xxiii. The initials ODEQ mean or refer to Oklahoma Department of
Environmental Quality Air Quality Division.
xxiv. The initials PM mean or refer to particulate matter.
xxv. The initials PSD mean or refer to prevention of significant
deterioration.
xxvi. The initials PTE mean or refer to potential to emit.
xxvii. The initials RCT mean or refer to Railroad Commission of
Texas, Oil and Gas Division.
xxviii. The initials SCADA mean or refer to Supervisory Control and
Data Acquisition.
xxix. The initials SIP mean or refer to State Implementation Plan.
xxx. The initials SO2 mean or refer to sulfur dioxide.
xxxi. The initials TAR mean or refer to Tribal Authority Rule.
xxxii. The initials TAS mean or refer to treatment as state.
xxxiii. The initials TIP mean or refer to Tribal Implementation
Plan.
xxxiv. The initials UDEQ mean or refer to Utah Department of
Environmental Quality.
xxxv. The initials VOC mean or refer to volatile organic
compound(s).
xxxvi. The initials VRU mean or refer to vapor recovery unit.
xxxvii. The initials WDEQ mean or refer to Wyoming Department of
Environmental Quality Air Quality Division.
Table of Contents
I. Background
II. Basis for Final Action
III. Final Action
IV. Major Issues Raised by Commenters and EPA's Response
A. Purpose and Scope of FIP
B. Legal Basis and Authority
C. Rule Development and Implementation
D. Applicability
E. Control Equipment and Requirements
F. Monitoring and Recordkeeping Requirements
G. Reporting Requirements
H. Cost Analysis
I. Public Notice
V. Summary of Final Rule and Significant Changes From the Proposed
and Interim Final Rule
A. Administrative Edits
B. Introduction
C. Compliance Schedule
D. Provisions for Delegation of Administration to the Three
Affiliated Tribes of the Mandan, Hidatsa, and Arikara Nation
E. General Provisions
F. Construction and Operational Control Measures
G. Control Equipment Requirements
H. Monitoring Requirements
I. Recordkeeping Requirements
J. Reporting Requirements
K. Effect on Permitting of Facilities
L. Registration Requirements
VI. Statutory and Executive Order Reviews
[[Page 17837]]
I. Background
On August 1, 2012, we signed a proposed rulemaking to establish a
Federal Implementation Plan (FIP) for oil and natural gas production
facilities located on the Fort Berthold Indian Reservation (FBIR). We
also signed an interim final rule concurrent with the proposed action
because we found good cause under Section 553(b)(B) of the
Administrative Procedure Act, 5 U.S.C. 551 et seq. that notice-and-
comment are impracticable, unnecessary or contrary to the public
interest in this instance. The proposal and concurrent interim final
rule were published in the Federal Register on August 15, 2012 (77 FR
48878), and residents of the FBIR, as well as industry representatives
and environmental groups commented on the proposed rule. During the 60-
day comment period that ended on October 15, 2012, we also held a
public hearing in New Town, North Dakota on September 12, 2012. We
received seven written comments during the comment period and 12 people
provided oral testimony at the public hearing. This Federal Register
action announces our final action on the proposed regulations.
In promulgating this rule, the EPA is exercising its discretionary
authority under Sections 301(a) and 301(d)(4) of the Clean Air Act
(CAA) to promulgate regulations as necessary to protect tribal air
resources. Promulgating this final rule addresses an important initial
step to fill a regulatory gap between state and federal requirements
with regard to controlling volatile organic compound (VOC) emissions
from oil and natural gas operations on the FBIR. There is no other
federal rule, including the recently finalized New Source Performance
Standards (NSPS) and National Emissions Standards for Hazardous Air
Pollutants (NESHAP) for the Oil and Natural Gas Sector (NSPS OOOO and
NESHAP HH),\1\ that establishes regulations for the particular oil and
natural gas production operations that exist on the FBIR. This is in
contrast to oil and natural gas operations off the Reservation, which
are governed by the North Dakota Department of Health (NDDoH)
regulations and North Dakota Industrial Commission (NDIC) regulations
within the State of North Dakota's jurisdiction. The NDDoH requirements
were developed with an understanding of the high VOC emissions and
infrastructure constraints that exist in the region. Consistent with
the regulatory structure that exists off the FBIR, and NSPS OOOO, this
rule has requirements for VOC emissions control and reductions,
monitoring, recordkeeping, and reporting. This rule also establishes
requirements that are clear and legally and practicably enforceable.
---------------------------------------------------------------------------
\1\ ``Oil and Natural Gas Sector: New Source Performance
Standards and National Emission Standards for Hazardous Air
Pollutants Review, Final Rule'' Federal Register 77:159 (16 August
2012) p. 49490. The regulations can be accessed at https://www.epa.gov/airquality/oilandgas/actions.html and are included in
the docket for this rule.
---------------------------------------------------------------------------
We developed this rule in consultation with the Three Affiliated
Tribes of the Mandan, Hidatsa, and Arikara Nation. As part of this
consultation, we evaluated the oil and natural gas activities and
sources of VOC emissions that could impact air resources on the
Reservation and the differences in the VOC emission reduction
requirements for those facilities operating on the FBIR compared to
those facilities operating in NDDoH jurisdiction. The final rule we are
promulgating today establishes regulations for oil and natural gas
production and storage operations specific to the FBIR and applies to
all lands on the FBIR, which is defined by the Act of March 3, 1891 (26
Statute 1032) and which includes all lands added to the Reservation by
Executive Order of June 17, 1982.
We drafted the requirements that are consistent to the greatest
extent practicable with the most relevant aspects of neighboring state
and local rules concerning the air pollutant emitting activities on the
FBIR. We do not intend, nor do we expect, this regulation to impose
significantly different regulatory burdens upon industry or the
residents of the FBIR than those imposed by the rules of state and
local air agencies in the surrounding areas. We evaluated the
regulations imposed by other oil and natural gas producing state
jurisdictions, NDDoH, NDIC, and NSPS OOOO. Included in the docket for
this rule are copies of the regulations and guidance that we considered
in this process, as well as a technical support document \2\ (TSD)
explaining the requirements.
---------------------------------------------------------------------------
\2\ The Technical Support Document includes a more detailed
explanation of the development of this FIP. It can be found in the
docket for this rule, Docket ID: EPA-R08-OAR-2012-0479, which can be
accessed at: https://www.regulations.gov.
---------------------------------------------------------------------------
We requested comments on all aspects of our proposed action and
provided a 60-day comment period. During the comment period, we
received comments on our proposed rule that supported our proposed
action and that were critical of our proposed action. After evaluating
all the comments that were received, we are taking final action to
respond to the comments we have received, explain the basis for our
action, and promulgate the final rule. In this final rule, also
referred to as the Federal Implementation Plan for Oil and Natural Gas
Well Production Facilities; Fort Berthold Indian Reservation (Mandan,
Hidatsa, and Arikara Nation), North Dakota, we are making certain
revisions based on the information provided by commenters and regulated
entities. This preamble to the final rule responds to the issues raised
by commenters and describes the final rule and significant changes from
the proposed rule.
II. Basis for Final Action
This Federal Register action announces the EPA's final action on
the proposed regulations of August 15, 2012. In promulgating this rule,
the EPA is exercising its discretionary authority under Sections 301(a)
and 301(d)(4) of the CAA to promulgate such implementation plan
provisions as are necessary or appropriate to protect air quality
within the FBIR, specifically identified in 40 CFR part 49, subpart K--
Implementation Plans for Tribes--Region VIII. After evaluating air
quality issues for the FBIR, the EPA was concerned that there was a gap
in air quality requirements for oil and natural gas production
facilities on the FBIR under the CAA and its implementing regulations.
Our proposed rule in August 2012 was generally based upon the
aspects of neighboring NDIC and NDDoH regulations most relevant to the
oil and natural gas production VOC-emitting activities occurring on the
FBIR. We acknowledged that there were some differences between the
requirements in the proposed rule and those in the NDIC and NDDoH
regulations, most notably additional monitoring requirements. These
differences were necessary to meet the standards for promulgating FIPs.
Included in the docket for the proposed rulemaking were copies of all
of the state rules that the EPA considered in this process, as well as
a TSD comparing the proposed regulations with the state regulations and
a description of why the EPA believed the proposed rule was
appropriate.
During the public comment period, a number of FBIR residents,
industry representatives and the regulated entities, environmental and
resident advocate organizations, and tribal government agencies
submitted comments on the rule proposed by the EPA and offered
suggestions for improving the proposed rule. We have fully considered
all substantive public comments on our proposal and have
[[Page 17838]]
concluded that certain changes are warranted. Those changes are
discussed in Section V of this notice. However, the EPA does not
intend, nor does it expect, these regulations to impose significantly
different regulatory burdens upon industry or the residents within the
FBIR than those imposed by the rules of the NDIC and NDDoH in the
surrounding areas.
III. Final Action
In this action, we are promulgating a Reservation-specific FIP to
establish enforceable control requirements for reducing VOC emissions
from oil and natural gas production activities on the FBIR in North
Dakota. This final rule replaces the interim final rule promulgated on
August 15, 2012 (77 FR 48878) in all intents and purposes on the
effective date of the final rule.
IV. Major Issues Raised by Commenters and EPA's Response
A. Purpose and Scope of FIP
Comment: Multiple commenters described the ways in which the
existing oil and natural gas development had negatively affected their
communities. For example, commenters described black smoke, visible
soot, and strong gas odors. Other commenters expressed support of the
EPA's decision to cover existing wells in the FIP.
Response: We acknowledge the concerns expressed by the commenters
related to oil and natural gas production activities on the FBIR. The
purpose of this FIP, in part, is to address the potential impacts of
VOC emissions caused by the oil and natural gas production occurring in
the region. By requiring process equipment at oil and natural gas
production facilities to be operated with specific air emission
controls, under specific operating conditions and following specific
procedures, this FIP will help address these concerns. We are requiring
that operations at these facilities be monitored and records be kept
such that any improper process or emission control equipment operated
by the owner or operator at a facility can be identified and remedied
by the EPA through enforcement of this FIP. The public can report
possible harmful environmental activity on the EPA's Web site at https://www.epa.gov/tips/.
We acknowledge the commenters support of the FIP to cover existing
wells. As discussed in the TSD, one goal of this FIP was to provide an
avenue of compliance with the CAA for those companies subject to CAFO
agreements. Our primary goal, as always is with regard to regulations
developed under the CAA, was to ensure increased protection to the
public health and the environment. This FIP provides these benefits
through promulgation of enforceable requirements to limit VOC emissions
from facilities that constructed prior to the effective date of the
interim final FIP.
Comment: One commenter stated that the EPA needs to control air
quality because hydraulic fracturing (``fracking'') is under-regulated.
Response: The majority of oil and natural gas wells drilled today
are hydraulically fractured. Hydraulic fracturing occurs when wells are
being completed and recompleted. NSPS OOOO ensures that VOC emissions
are controlled from the completion and recompletion of natural gas
wells. Additionally, this FIP requires that owners and operators of oil
and natural gas production facilities on the FBIR reduce by at least
90% the VOC emissions from casinghead natural gas during the completion
or recompletion of any oil and natural gas well. Together, these recent
regulatory actions will provide significant control of emissions from
hydraulic fracturing activities.
Comment: Several commenters stated that the EPA should set methane
standards in the final FIP noting that methane is a greenhouse gas
(GHG) with a high carbon dioxide (CO2) equivalent, and that
leaked methane therefore negatively influences climate change. These
same commenters also stated that the EPA already requires control
technologies that could facilitate emissions standards for methane and
that tribes have particular interest in mitigating climate change
because they are disproportionately impacted by it.\3\ The commenters
also stated that leaked methane decreases a potentially significant
revenue stream for producers. Another commenter stated that flaring
creates significant CO2 pollution, which contributes to
climate change.
---------------------------------------------------------------------------
\3\ Commenter cites ``EPA Tribal Science Council, Tribal Science
Priority'' at 1 (June 2011). A copy of the document is included in
the docket for this rule, Docket ID: EPA-R08-OAR-2012-0479, which
can be accessed at: https://www.regulations.gov.
---------------------------------------------------------------------------
Response: We had a very specific purpose for developing this FIP,
which was to regulate VOC emissions from oil and natural gas production
operations on the FBIR which represented the largest source of air
quality concerns at this time. While this rule does not directly
regulate other pollutants subject to regulation under the CAA, such as
the GHGs methane and CO2, it does result in significant
reductions of GHGs because of the substantial methane reduction as a
co-benefit of the required VOC control.
Comment: Other commenters expressed concern about the dust now
prevalent in the area. The commenters stated that excessive dust was
often seen in the air as well as on trees and grass. Some commenters
insisted that oil and trucking companies should participate in control
of dust in the area. One commenter stated that visible emissions have
not been responded to by the EPA or the Three Affiliated Tribes of the
Mandan, Hidatsa, and Arikara Nation.
Response: This FIP is focused on emissions of VOCs, and regulating
fugitive dust resulting from oil and natural gas production activities
on the FBIR was not within the scope of the rulemaking. If the EPA
determines it is necessary to regulate other pollutants, we will
address those at that time. Generally, dust from road traffic is a
local issue and the public should contact the local environmental or
health agency with these concerns. The public can report possible
harmful environmental activity on the EPA's Web site at https://www.epa.gov/tips/.
Comment: Several commenters noted a significant increase in truck
traffic since oil and natural gas production on the FBIR had begun. One
commenter noted that the incidence of traffic accidents, often fatal,
has significantly increased on the FBIR since production has begun.
Response: Traffic in North Dakota and on the FBIR is regulated by
the Three Affiliated Tribes of the Mandan, Hidatsa, and Arikara Nation
or the United States Department of Transportation, and not by the EPA
and thus is not within the EPA's authority to address.
Comment: One commenter discussed being bothered by noticeable
diesel emissions from the increased truck traffic. Another commenter
noted that an oil rig was polluting in close proximity to a school.
Response: This FIP does not regulate the exhaust emissions from the
trucks or oil rigs. These sources of emissions meet the definition of
on-road and non-road motor vehicles (mobile sources) under the CAA and
are subject to regulations under those provisions. This FIP only
regulates stationary oil and natural gas production sources. A
stationary source is defined in the CAA (42 U.S.C. 7602(z)) to mean
``generally any source of an air pollutant.'' The definition
specifically excludes those emissions resulting directly from an
internal combustion engine for transportation purposes or from a
nonroad engine or nonroad vehicle as defined in 42 U.S.C. 7550. This
rule however does not
[[Page 17839]]
exempt the owners and operators from any other requirements under the
CAA to minimize pollutants and control emissions from these sources.
Comment: Some commenters stated that oil and natural gas
development had also negatively impacted water quality. One commenter
stated that the water at her house is undrinkable and is often too poor
to be used for other common functions like laundry. Some commenters
stated that they had witnessed trucks dumping waste from oil and
natural gas production in unauthorized locations, including the ground
near Skunk Bay.
Response: We acknowledge the concerns expressed by the commenters
in regard to the effect that oil and natural gas production activities
may have on water quality. Our authority to issue this rule, however,
falls under the CAA. Water pollution on the FBIR is addressed through
separate regulations established under the Clean Water Act (CWA).
Additional information about the CWA can be found at https://www.epa.gov/regulations/laws/cwa.html. In addition, the public can
report possible harmful environmental activity on the EPA's Web site at
https://www.epa.gov/tips/.
Comment: One commenter recommended that the EPA explore voluntary
partnerships with FBIR producers in order to deploy best practices for
gas capture and use. Commenter stated that this may allow FBIR
producers to demonstrate the feasibility and benefits of comprehensive
gas capture at co-producing sites, and in doing so encourage these
practices for other producers in the Bakken and elsewhere.
Response: We appreciate the commenter's suggestion; however, such a
partnership is outside of the scope of this FIP and 40 CFR part 49. The
comment is more appropriately addressed through the EPA's voluntary
programs, such as the Natural GasSTAR Program.\4\ Therefore we have
forwarded this comment on to the Natural GasSTAR Program for their
consideration.
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\4\ Information on the EPA's Natural Gas STAR Program is
available online at: https://www.epa.gov/gasstar/, Accessed November
15, 2012.
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B. Legal Basis and Authority
Comment: Some commenters disagreed with our assertion that the rule
is needed and justified to mitigate hazards to the public health and
the environment, stating that actual emissions are much lower than
potential emissions, and are low enough to present no hazard to public
health or the environment. The commenters further stated that rather
than the protection of the public health and environment, the purpose
of this FIP is to solve the ``legal and hypothetical problem'' of
ensuring potential emissions do not exceed regulatory applicability
thresholds, such as the PSD thresholds. The commenters stated that the
EPA proposed the FIP not to improve already good air quality\5\ or to
satisfy CAA requirements, but because many FBIR operators need
preconstruction permits and the EPA lacks adequate time or resources to
issue those permits by the time the Consent Agreement and Final Orders
(CAFOs) \6\ governing the sources expire.
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\5\ Commenter references the interim final rule at 77 FR 48886.
\6\ The FBIR CAFOs are included in the docket for this rule,
Docket ID: EPA-R08-OAR-2012-0479, which can be accessed at: https://www.regulations.gov.
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Several commenters support the proposed FIP and also agree that we
have just cause to mitigate hazards to the public health and the
environment and with our assertion and that we are acting in accordance
with our trust responsibilities to protect the public health and
environment in Indian country.
Response: The purpose of this FIP is to address potential impacts
to the public health and the environment. It also solves some of the
unusual challenges that owners and operators on the FBIR face with
regard to compliance with the permitting requirements of the CAA.
However, our primary purpose for developing rules to regulate air
emissions is to meet the requirements of the CAA to protect the public
health and the environment by providing those living on the Reservation
the same level of air quality and health protection as people living
outside the Reservation. So, while this FIP solves some of the
challenges that the owners and operators on the FBIR face with regard
to requirements of the CAA, or more specifically the PSD permitting
requirements, the primary focus is to prevent the potential degradation
of the air quality on the FBIR.
The CAA is a comprehensive federal law that regulates air emissions
from stationary and mobile sources. Among other things, this law
authorizes us to establish National Ambient Air Quality Standards
(NAAQS) to protect public health and the environment. Amendments to the
CAA codified the PSD preconstruction permitting program to protect the
public health and the environment from any actual or potential adverse
effects which may reasonably be anticipated to occur notwithstanding
attainment and maintenance of the NAAQS.
Because of the high quantity of VOC emissions present in the oil
and natural gas operations in the Bakken formation, the absence of
infrastructure to capture excess volatile liquids, and the regulatory
gap that rendered the use of control technology unenforceable prior to
the FIP, some sources had potential emissions that would have required
major source permits. These preconstruction PSD permits are one
mechanism available to the EPA to assure that emissions increases
associated with economic development do not threaten the NAAQS. Under
the Federal Tribal NSR rule, sources located on the FBIR may also
obtain synthetic minor NSR permits to limit their emissions below major
source levels. Either of these options would require that the EPA
review and issue several hundred air permits to emissions limitations
similar to those required by this FIP. We determined, therefore, that
issuing this FIP, and imposing emission limitations for these sources
at one time was a more efficient and streamlined mechanism than issuing
individual permits. We believe that this is the best way to address the
potential harm that these previously unregulated VOC emissions would
create, and ensure that we are not inhibiting the growth of oil and
natural gas due to the permitting process, which could put the Tribe at
an economic disadvantage.
Finally, while actual emissions for some sources may be lower than
potential emissions, there are no federally and practicably enforceable
emission control requirements for the affected equipment limiting the
potential to emit. This rule imposes emission limitations that are
federally and practicably enforceable.
Comment: Several commenters stated that by proposing to adopt this
FIP, the EPA is stepping into the shoes of the Tribes and acting as the
local air pollution control authority. The FIP includes a comprehensive
set of control measures for oil and natural gas operations--imposing
requirements on such operations merely because they exist and not
because they have engaged in an activity that triggers a regulatory
requirement, such as building a new source or modifying an existing
source such that a PSD permit or a synthetic minor NSR permit is
needed. In other words, the EPA is adopting what would otherwise amount
to a State Implementation Plan (SIP) or TIP for the FBIR. The authority
for such a control program necessarily flows from section 110(a), which
specifies the measures that a SIP may include. This section of
[[Page 17840]]
the CAA specifies that a SIP may ``include enforceable emission
limitations and other control measures, means, or techniques * * * as
may be necessary or appropriate to meet the applicable requirements of
this chapter.'' CAA section 110(a)(2)(A) (emphasis added). Thus, the
EPA may adopt as part of this FIP only those measures that are needed
to attain or maintain NAAQS or to meet other specified CAA applicable
requirements.
Response: We disagree; the commenter is mistaken that the
underlying authority for this FIP is found in Section 110(a) of the
Act. Section 301(d) of the CAA, 42 U.S.C. 7601(d), directs us to
promulgate regulations specifying the provisions of the Act for which
it is appropriate to treat Indian tribes in the same manner as states.
Pursuant to this statutory directive, the EPA promulgated regulations
entitled, ``Indian Tribes: Air Quality Planning and Management'' (TAR)
(63 FR 7254, February 12, 1998). Our regulations delineate the CAA
provisions for which it is appropriate to treat tribes in the same
manner as a state. See 40 CFR 49.3, 49.4. Among those provisions for
which we determined such treatment was inappropriate are CAA section
110(a)(1) (SIP submittal and implementation deadlines) and CAA section
110(c)(1) (directing the EPA to promulgate a Federal Implementation
Plan (FIP) ``within 2 years'' after we find that a state has failed to
submit a required plan, or has submitted an incomplete plan, or within
2 years after we disapproved all or a portion of a plan). See 40 CFR
49.4(a), (d); 63 FR 7262-7266, February 12, 1998.
The TAR preamble clarified that by including CAA section 110(c)(1)
on the Sec. 49.4 list, ``EPA is not relieved of its general obligation
under the CAA to ensure the protection of air quality throughout the
nation, including throughout Indian country. In the absence of an
express statutory requirement, EPA may act to protect air quality
pursuant to its ``gap-filling'' authority under the Act as a whole.
See, e.g. CAA section 301(a).'' (63 FR 7265, February 12, 1998). The
preamble confirmed that ``EPA will continue to be subject to the basic
requirement to issue a FIP for affected tribal areas within some
reasonable time.'' Id. (referencing Sec. 49.11(a) which provides that
the Agency will promulgate a FIP to protect tribal air quality within a
reasonable time if tribal efforts do not result in adoption and
approval of tribal plans or program).\7\
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\7\ Section 49.11(a) states that the Agency, ``[s]hall
promulgate without unreasonable delay such federal implementation
plan provisions as are necessary or appropriate to protect air
quality, consistent with the provisions of sections 301(a) and
301(d)(4), if a tribe does not submit a tribal implementation plan
meeting the completeness criteria of 40 CFR part 51, Appendix V, or
does not receive EPA approval of a submitted tribal implementation
plan.'' 40 CFR 49.11(a).
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The preamble to the TAR set forth our view articulated in the
proposed rule that, based on the ``general purpose and scope of the
CAA, the requirements of which apply nationally, and on the specific
language of Sections 301(a) and 301(d)(4), Congress intended to give to
the Agency broad authority to protect tribal air resources.'' Id. at 63
FR 7262. It further discussed our intent to ``use its authority under
the CAA `to protect air quality throughout Indian country' by directly
implementing the Act's requirements in instances where tribes choose
not to develop a program, fail to adopt an adequate program or fail to
adequately implement an air program.'' Id.
The NDDoH, the CAA permitting authority for areas of North Dakota
outside of Indian country, including outside of the FBIR, has
promulgated rules to control emissions from oil and natural gas
production facilities. Since there is not currently an approved TIP
specifically covering the reduction of VOC emissions related to natural
gas emissions from oil and natural gas production facilities on the
FBIR, a lack of regulation exists with regard to such facilities
operating within the exterior boundaries of the Reservation. This FIP
establishes legally and practicably enforceable requirements to control
and reduce VOC emissions. Therefore, in this rule, we determined that
it is necessary and appropriate to exercise our discretionary authority
under sections 301(a) and 301(d)(4) of the CAA and 40 CFR 49.11(a) to
promulgate a FIP to remedy an existing regulatory gap under the Act
with respect to oil and natural gas operations on the FBIR.
Comment: One commenter was concerned that the Tribe would have
enforcement authority and be allowed to act arbitrarily and
capriciously with regard to shutting down operations and requested that
the requirements of this rule be enforced by the federal government.
The commenter stated that the Three Affiliated Tribes of the Mandan,
Hidatsa, and Arikara Nation should not be allowed to enforce the rule
because its elected officials have economic interest in the oil and
natural gas industry, making them conflicted.
Response: At this time, EPA has not delegated to the Three
Affiliated Tribes of the Mandan, Hidatsa, and Arikara Nation the
authority under these regulatory provisions to enforce the provisions
of this FIP. The provisions in Sec. 49.4162 of the Code of Federal
Regulations establish the steps by which the Three Affiliated Tribes of
the Mandan, Hidatsa, and Arikara Nation may request delegation to
assist us with the administration of this rule. As described in the
regulatory provisions and the preamble to the proposed rule, any such
delegation will be accomplished through a delegation of authority
agreement between the EPA Region 8 Administrator and the Three
Affiliated Tribes of the Mandan, Hidatsa, and Arikara Nation. In the
event such an agreement is reached, the rule would continue to operate
under federal authority throughout the FBIR, and the Three Affiliated
Tribes of the Mandan, Hidatsa, and Arikara Nation would assist us with
administration of the rule to the extent specified in the delegation
agreement.
C. Rule Development and Implementation
Comment: One commenter indicated that the State of North Dakota was
issuing permits to drill on the FBIR and asserted that the State has
been giving out drilling permits ``like candy,'' leading to an
overwhelming level of oil and natural gas development and increase in
pollution on the FBIR. The commenter stated that the Tribe did not
have, nor did they develop, necessary regulations when development
began, and that the Tribe, as well as the EPA, is now playing ``catch-
up.''
Response: We acknowledge the commenter's concern with increased oil
and natural gas development on the FBIR, as well as increased
development under the State of North Dakota's jurisdiction and the need
for reservation-specific regulations to protect public health and the
environment. We note that the State of North Dakota does not have
jurisdiction over development on the FBIR. As discussed in the preamble
for the interim final rule, we first became aware of the need to
address VOC emissions from these operations in August of 2011. At that
time, a significant number of entities engaged in oil and natural gas
operations on the FBIR informed us that the emissions of regulated air
pollutants, including VOC, were significantly larger than previously
understood and larger than emissions in other areas, due to the
geologic characteristics and infrastructure challenges in the Bakken
formation. At
[[Page 17841]]
that time, we immediately took measures to ensure that VOC emissions
were appropriately controlled by entering into CAFOs with the owners/
operators to implement VOC controls. We then developed and promulgated
this FIP as an interim final rule to immediately establish federally
and practicably enforceable emission control requirements for the
affected equipment. In addition, given the number of existing
facilities that were operating as unregulated sources, we determined
that existing facilities should also be subject to the FIP. We believe
the series of actions taken to address the unregulated sources of VOC
emissions on the FBIR occurred as soon as practicable after becoming
aware of the issue.
Comment: One commenter stated that the EPA had accelerated
development of this FIP without consideration of its impact on the
community to avoid disrupting the pace of oil and natural gas
development. Another commenter stated that this FIP is not strict
enough, citing the estimated potential long-term development of 1,000
oil and natural gas facilities by 2029 as discussed in the interim
final rule (77 FR 48887).
Response: We disagree with the assertion that the expedited process
for developing this FIP did not take into consideration the impacts of
oil and natural gas development on the community. The mitigation of the
air quality impact of oil and natural gas development on the FBIR was a
priority when developing this rule. This rule will reduce VOC emissions
from existing operations and limit the amount of VOC emissions from
potential new development. Our intent is to level the health
protections between the residents living on the FBIR and the residents
living in the State of North Dakota. In other words, the EPA intends
that the FBIR residents receive equivalent air quality protections as
those residing in the State. We acted quickly in developing this FIP in
order to provide those protections as soon as possible and avoid
unnecessary disruption to oil and natural gas development. While the
FIP development process has been quick, as discussed in this notice we
have provided for full public participation and fully responded to all
concerns.
We also disagree that the FIP is not strict enough. This FIP
establishes requirements to control air pollution in the form of VOC
emissions from oil and natural gas production and storage operations on
the FBIR, comparable to those requirements developed by state
permitting authorities. In addition, this FIP imposes emission
reduction requirements that are robust and consistent with the control
technology requirements for the oil and natural gas production and
storage industry under NSPS OOOO.
Comment: One commenter stated that an environmental impact
statement (EIS) was not required prior to leasing the tribal land for
oil and natural gas development. The commenter noted that a
programmatic environmental assessment (EA) is being conducted, but
insisted that the more rigorous EIS should have been required. The
commenter questioned whether it was legal for the EIS requirement to be
bypassed, and stated that the requirements of the National
Environmental Policy Act (NEPA) had been ``minimized.'' Therefore, the
commenter asserted that area residents were denied the opportunity to
make statements regarding the impact of oil and natural gas development
on their lives. Another commenter stated that the lack of adequate
public notice for the EA was not compliant with NEPA and environmental
justice.
Response: This FIP only regulates the VOC air pollutant emissions
generated by the well completion and production and storage operations
on the FBIR and is not subject to the requirements of NEPA (EIS or EA).
A FIP is an action under the CAA and Section 7(c) of the Energy Supply
and Environmental Coordination Act of 1974 (15 U.S.C. 793(c)(1))
exempts actions under the CAA from the requirements of NEPA,
specifically this section reads ``* * * (c) Major federal actions
significantly affecting the quality of the human environment (1) No
action taken under the Clean Air Act [42 U.S.C. 7401 et seq.] shall be
deemed a major Federal action significantly affecting the quality of
the human environment within the meaning of the National Environmental
Policy Act of 1969 [42 U.S.C. 4321 et seq.].'' Therefore a NEPA
analysis is not required for this FIP.
Leasing of the mineral rights and drilling of the oil and natural
gas wells is regulated by the Bureau of Indian Affairs (BIA) and the
Bureau of Land Management (BLM). Those federal agencies are undertaking
any applicable NEPA requirements when approving leasing and drilling
activities.
Comment: Many commenters asserted that this FIP falls short of its
stated purpose because some facilities' potential to emit (PTE) of VOCs
or any other regulated NSR pollutant may exceed the applicability
thresholds for PSD permitting resulting in the need for a synthetic
minor NSR permit issued under Federal Tribal NSR Rule (if PSD
permitting is to be avoided) even after applying the legally and
practicably enforceable emission reductions provided in this rule (77
FR 48885). Several commenters stated that the EPA should declare in the
final FIP that all sources that become minor under the Federal Tribal
NSR rule will be considered ``true minor'' sources. More specifically,
commenters claim that sources treated as synthetic minor sources under
this FIP could not install new wells for the foreseeable future because
the EPA has not developed an expeditious process for issuing synthetic
minor NSR permits.
Another commenter questioned why owners and operators working
within the FBIR would be allowed to exceed VOC emission standards.\8\
The commenter asked if there was any point in setting these standards
if permits could be obtained to exceed them.
---------------------------------------------------------------------------
\8\ The commenter is referring to the interim final rule Section
III.E. ``Effect on Permitting of Facilities.'' (77 FR 48885).
---------------------------------------------------------------------------
Response: The owners and operators subject to this FIP are not
allowed to exceed established standards, and nothing in this FIP is
intended to relieve the owners and operators of the responsibility to
comply with all federal environmental laws and rules. This rule does
not replace any requirement to obtain permission to construct under the
PSD regulations at 40 CFR 52.21 or the Federal Tribal NSR regulations
at 40 CFR 49.151; therefore, this FIP does not automatically create
``true minor'' status for those sources that become minor under the
Federal Tribal NSR Rule. Owners and operators complying with this rule
may still be required to obtain preconstruction permits to further
reduce VOC emissions or the emissions of other pollutants that are
regulated by the PSD and Federal Tribal NSR permitting regulations if
the emissions thresholds for these regulations are exceeded. Further,
this rule does not automatically make sources synthetic minor sources
for purposes of the PSD regulations. A synthetic minor source is
generally understood to include any source that would be major but for
a requested enforceable limitation. For example, a source can become a
synthetic minor source when the owner or operator requests a synthetic
minor NSR permit through the Federal Tribal NSR regulations to avoid
major source requirements of PSD and that request is approved and the
permit is issued.
This rule is similar to NSPS OOOO promulgated at 40 CFR part 60,
NESHAP HH promulgated at 40 CFR part 63, and the NDDoH regulations
specific to oil and natural gas production operations at Chapters 33-
[[Page 17842]]
15-07 and 33-15-20 of the North Dakota Administrative Code, none of
which replace CAA permitting requirements. Similar to the NSPS,
NESHAPs, and NDDoH regulations, this rule provides legally and
practicably enforceable restrictions for VOC emissions on an emission
unit specific basis. Any reductions realized by complying with this
rule can then be used to calculate the PTE of VOCs when determining
whether any CAA permitting may be required. In addition, the rule only
requires controls on VOC emissions, because of the high amount of
associated natural gas in the crude oil from the FBIR and the absence
of infrastructure to capture the natural gas emissions. Therefore, any
potential emissions of VOCs or any other criteria pollutant that exceed
the PSD permitting thresholds after taking credit for the enforceable
restrictions in this rule would still result in the requirement to
obtain a PSD permit for permission to construct. A synthetic minor NSR
permit to avoid the PSD permitting requirements can still be requested
through the Federal Tribal NSR regulations. Those facilities with
potential emissions of VOCs and all other criteria pollutants that are
below the PSD permitting thresholds and above the Federal Tribal NSR
permitting thresholds after complying with the requirements of this FIP
would be considered true minor sources under the Federal Tribal NSR
regulations.
Finally, regarding the commenter's claim that sources treated as
synthetic minor sources under this FIP could not install new wells for
the foreseeable future because the EPA has not developed an expeditious
process for issuing synthetic minor permits, the EPA has issued and
continues to issue synthetic minor permits to sources on the FBIR to
those who request them.
Comment: Several commenters requested that the EPA clarify that a
stationary source and corresponding minor NSR permitting requirements
apply to operations and equipment on a well pad and immediately
appurtenant operations. These commenters also urged the EPA to clarify
that geographically separated ``well pads and related operations''
should not be aggregated into one stationary source simply because they
are connected by gathering or production lines. The commenters asserted
that the EPA's use of the term ``integrally connected'' (77 FR 48885)
could create confusion as to what equipment and activities are
considered part of a facility. The commenters cited Summit Petroleum
Corp. v. EPA \9\ as an example of the EPA incorrectly aggregating
multiple wells, well pads and related facilities that were
geographically widespread into one single facility for the purposes of
the CAA. The commenters stated that such an approach is ``nonsensical''
and inconsistent with the CAA definition of ``stationary source.'' The
commenters also requested that the EPA explain the limited
circumstances in which aggregation into a ``facility'' or ``stationary
source'' is appropriate, and suggested the following as those
circumstances; When: (1) The operations share a single two-digit major
SIC code; (2) the operations are under common ownership or control; and
(3) the operations are physically contiguous or physically proximate.
The EPA should specify that functional interrelatedness should not be
used to determine physical proximity.
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\9\ Summit Petroleum Corp. v. EPA, Nos. 0904348, 10-4572 (Sixth
Cir. 2012) at 1. The document is included in the docket for this
rule, Docket ID: EPA-R08-OAR-2012-0479, which can be accessed at:
https://www.regulations.gov.
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Response: This action affects facilities operating on the FBIR in
North Dakota, and thus the 6th Circuit's Summit Petroleum decision
cited by the commenters does not apply.\10\ When the EPA issues permits
to sources that are also subject to this rule, the ultimate
determination regarding the scope of the stationary source to be
permitted will be made by implementing the stationary source definition
contained in the federal NSR and Title V regulations (40 CFR
52.21(b)(5) and (6), 71.2). Such determinations are highly fact
specific and will continue to be made on a case-by-case basis, applying
the relevant regulatory criteria to the facts of the oil and natural
gas production activities being permitted.
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\10\ Memo from Stephen D. Page, Director, Office of Air Quality
Planning and Standards, to Regional Air Division Directors, Regions
1-10, Applicability of the Summit Decision to EPA Title V and NSR
Source Determinations (Dec. 21, 2012), available at https://epa.gov/nsr/documents/SummitDecision.pdf and included in the docket for this
rule, Docket ID: EPA-R08-OAR-2012-0479, which can be accessed at:
https://www.regulations.gov.
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Comment: Several commenters stated that the final FIP should refer
to Bakken Pool wells located on the FBIR simply as ``oil wells'' or
``Fort Berthold Indian Reservation wells'' rather than using the
phrases ``oil and natural gas production wells'' or ``oil and natural
gas production facilities.'' The commenters asserted that using the
characterization ``oil wells'' is consistent with related EPA
rules.\11\ One commenter also stated that North Dakota permits refer to
these as oil wells. On the other hand, two commenters stated that they
support the inclusion of co-producing oil and natural gas wells, which
are defined as ``oil and natural gas production facilities'' in this
FIP.
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\11\ Commenter specifically mentions the ``New Source
Performance Standards for Crude Oil and Natural Gas Production,
Transmission and Distribution'' (40 CFR part 60, subpart OOOO) and
the ``Greenhouse Gas Reporting Rule'' (40 CFR part 98, subpart W).
---------------------------------------------------------------------------
Response: The reference to the Bakken Pool \12\ production
facilities as oil and natural gas production facilities in this FIP is
consistent with: (1) NDDoH regulations at 33-15-20 which defines an oil
well as ``any well capable of producing oil or oil and casinghead gas
from a common source of supply''; and (2) the NDDoH's Bakken Pool
Guidance \13\ (Bakken Pool Guidance) which refers to the facilities as
oil and gas production facilities, both of which form the basis of this
rule. We believe this reference adequately describes the affected
facilities under the FIP and is consistent with NDDoH regulations and
guidance.
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\12\ The Bakken Pool is defined as a compilation of crude oil
formations consisting of Bakken, Sanish and Three Forks formations.
\13\ Bakken Pool Oil and Gas Production Facilities Air Pollution
Control Permitting & Compliance Guidance, NDDoH Air Quality
Division, May 2, 2011. This guidance document was developed by the
Bakken VOC Task Force. The Bakken VOC Task Force was a collaboration
between the NDDoH and the owners and operators of oil and gas
operations producing from the Bakken Pool. A copy of the guidance
document is included in the docket for this rule, Docket ID: EPA-
R08-OAR-2012-0479, which can be accessed at: https://www.regulations.gov.
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We acknowledge the commenter's assertions that the facilities may
be described differently in other EPA regulations. Although the Bakken
Pool production wells on the FBIR would be considered oil wells based
on the discussions in NSPS OOOO and Subpart W (76 FR 80567), those
discussions do not adequately reflect the volume of natural gas
coproduced from a Bakken Pool well. NSPS OOOO and Subpart W are
national rules, and therefore, the discussions they contain must be
broad enough to apply nationwide. Since this a reservation-specific
FIP, we believe it is appropriate to use a more focused definition, as
did the State of North Dakota in the Bakken Pool Guidance, due to the
unique nature of the oil being produced from the Bakken Pool.
D. Applicability
Comment: Several commenters stated that the FIP should establish a
minimum emissions threshold for applicability, which exists in NSPS
OOOO.
Response: The only minimum emission threshold for applicability
that
[[Page 17843]]
exists in NSPS OOOO and could apply to emission units regulated under
this FIP is the 6 tpy applicability threshold for storage tanks. While
this FIP does not provide the same applicability threshold for tanks as
that found in NSPS OOOO, it does exempt storage tanks that are or
become subject to the requirements of NSPS OOOO. See Sec. 49.4164(f).
However, several tanks operating on the FBIR prior to the applicability
date of NSPS OOOO are not subject to NSPS OOOO. Therefore, since these
tanks are not subject to NSPS OOOO and do not have a minimum emissions
threshold for applicability, we decided that it was appropriate to
regulate these tanks in a manner consistent with NDDoH requirements for
tanks at oil and natural gas production facilities outside the FBIR.
Specifically, the Bakken Pool Guidance at Appendix D and this FIP at
Sec. 49.4164(d)(2)(ii), allow for a reduced VOC destruction efficiency
and the use of pit flares where the PTE of VOCs from the aggregate of
all produced oil storage tanks and produced water storage tanks
interconnected with produced oil storage tanks at an oil and natural
gas production facility is less than, and reasonably expected to remain
below, 20 tons in any consecutive 12-month period. The commenters
failed to provide any supporting information on appropriate
applicability thresholds for the other production equipment regulated
under this FIP. As previously discussed, we believe the volume of VOC
emissions from oil and natural gas operations on the FBIR warrants
specially tailored regulation, which we have developed in this FIP, and
which NDDoH developed in their Bakken Pool Guidance. At this time, we
do not have sufficient information to establish minimum thresholds for
other production equipment.
Comment: Several commenters stated that the EPA should clarify that
the FIP statements ``[t]he completion date is considered the date that
construction at an oil and natural gas production facility has
commenced'' (77 FR 48885), and ``[t]he recompletion date is considered
the date that a modification has occurred at an oil and natural gas
production facility'' (77 FR 48885) are for the purposes of determining
whether this FIP applies to a particular oil production facility and
does not apply to other EPA rules or programs.
Response: We agree that the suggested clarification is necessary.
We have added language to the applicable provision (Sec. 49.4161(b))
to indicate that the correlation of the initiation of well completion
operations and well recompletion operations to the dates that
construction and modifications commence is specific to this rule. In
addition, we have changed the language to clarify that the compliance
date is upon initiation of well completion operations and well
recompletion operations.
Comment: Several commenters disagree with the EPA's assertion
contained in the NSPS OOOO that recompletion of an existing well
constitutes a modification. Because the EPA acts in accordance with the
NSPS OOOO regarding this position, the commenters restated the position
they had voiced in comments on the proposed NSPS OOOO. The commenters
concluded that this same error should not be perpetuated in the final
FIP.
Response: The issue of what constitutes modifications under CAA
section 111 was decided by EPA in the prior rulemaking and is not being
reopened here. While we are not statutorily compelled to use the same
definition here, we think it is appropriate to do so and commenters
have not provided a policy basis on which to revisit EPA's conclusion.
As explained in detail in section IX.A. of the preamble for the final
Federal Register notice of NSPS OOOO (77 FR 49510), a completion
operation associated with refracturing is considered a modification
under CAA section 111(a) because a physical change occurs to the well
resulting in emissions increases during the recompletion operation.
When determining applicability for the rule, we used August 12, 2007,
which is the earliest well completion date identified in the CAFOs and
thus the earliest well completion date information available to the EPA
at the time of the rulemaking. Due to the nature of operations
producing from the Bakken Pool and the significant amount of co-
produced natural gas emissions, it is important that modified
facilities are required to control emissions from affected equipment.
We believe including the definition of a modified facility in the final
FIP is important because it will require the control of emissions from
the recompletion of any existing well that was completed prior to
August 12, 2007 that the agency may not have been aware of at the time
of the rulemaking and that would not be subject to the rule prior to a
modification.
Comment: One commenter urged the EPA to include pollution control
requirements for dehydration units, pneumatic controllers and pumps,
and compressors, stating that these sources could be significant
sources of pollution. The commenter requested that the EPA incorporate
the requirements for compressors and pneumatics from the NSPS OOOO, at
a minimum.
Response: We agree with the commenter that dehydration units,
pneumatic controllers and pumps, and compressors are other sources of
air pollution that may be operating at the oil and natural gas
production facilities on the FBIR. We reviewed information provided in
154 applications for synthetic minor NSR permits submitted to the
Region 8 office \14\ during the development of the FIP. Based on these
applications, we were able to determine that the most significant
sources of the VOC emissions are the pieces of equipment used to
produce the oil and natural gas during well completions, phase
separation of the extracted reservoir fluids (heater-treater), and the
temporary storage of the crude oil (tanks). The information in the
applications indicates pneumatic devices, dehydration units,
compressors, and associated fugitive emissions listed in the
applications were minor sources of VOC emissions when compared to other
emission units. Therefore, requirements for this equipment have not
been included in this rule. If we determine at a later date that there
is a need for control of VOC emissions from oil and natural gas
production equipment and operations not covered by this rule, we may
propose additional FIPs or propose supplements to this FIP.
---------------------------------------------------------------------------
\14\ The applications can be found in the docket for this rule,
Docket ID: EPA-R08-OAR-2012-0479, which can be accessed at https://www.regulations.gov.
---------------------------------------------------------------------------
Comment: Several commenters stated that the EPA should remove all
requirements applicable to heater-treater combustion devices from the
FIP. The commenters asserted that the use of heater-treater combustion
devices can already be taken into account when determining PTE because
they are ``inherent process equipment,'' and that additional
requirements for these devices are therefore unnecessary. The
commenters cited criteria from the EPA letters \15\ and the Compliance
Assurance Monitoring (CAM) rulemaking \16\ to
[[Page 17844]]
argue that heater-treater combustion devices must be considered
inherent process equipment based on those criteria.
---------------------------------------------------------------------------
\15\ Letter from EPA to Mr. Timothy J Mahin, Intel Government
Affairs, dated November 27, 1995; see also Letter from EPA to Edward
R. Herbert III, Director of Environmental Affairs, National Ready
Mixed Concrete Association, July 10, 2002, included in the docket
for this rule under Docket ID: EPA-R08-OAR-2012-0479, which can be
accessed at: https://www.regulations.gov.
\16\ ``CAM Response to Comments, Part III,'' at 6-7, October 2,
1997, available online at https://www.epa.gov/airtoxics/cam/ricam.html and included in the docket for this rule under Docket ID:
EPA-R08-OAR-2012-0479, which can be accessed at: https://www.regulations.gov.
---------------------------------------------------------------------------
The commenters stated that the EPA's description of the heater-
treater combustion device requirement in the FIP mandates the use of
such devices at oil facilities, primarily for safety and product
recovery, and does not address air quality concerns (77 FR 48883-
48884).
The commenters also stated that the possibility of some oil
facilities operating without heater-treater devices is not an
appropriate justification for the FIP requirements, because any
facilities operating as such would be in clear violation of standard
operating procedures which ensure safe working conditions. The
commenters insisted that the EPA should not base this justification on
``unsupported assumptions'' that standing laws are being violated or
inadequately enforced.
Response: We acknowledge that the preamble at 77 FR 48883 states
that the oil/natural gas/water emulsion from the production wells is
transported through 2-phase separators (separators), which are an
inherent component of the pipeline. We also state in the same paragraph
that following the 2-phase separator, the emulsion enters a 3-phase
separator (heater-treater), which is a necessary step in the production
process and produces gas that is separated from the emulsion. However,
until the separated gas from the heater-treater is captured as product
or used in some other beneficial way at the facility (e.g., a fuel
source for gas burning equipment) it is a significant source of the
high volume VOC emissions we determined requires control to protect
public health and the environment on the FBIR. Throughout the
rulemaking process, one of our priorities was to equalize the
requirements that apply to sources operating in the State of North
Dakota's jurisdiction with the requirements that apply to sources
outside of the State's jurisdiction. The NDIC regulations found in the
Control of Oil and Gas Resources at Chapter 38-08-06 require that
natural gas from the heater-treaters be routed to a natural gas
gathering pipeline as soon as practicable. When a pipeline is not
available, the natural gas produced in the heater-treater process is
required to be routed to a control system or device. While we
acknowledged in the preamble for the interim final rule that the
purpose of the NDIC requirements was principally for safety and product
recovery reasons, we also acknowledged that the requirements for
heater-treaters were modeled after the Bakken Pool Guidance which
requires that the emissions from heater-treaters be controlled.
E. Control Equipment and Requirements
Comment: One commenter stated that flares of roughly 40 feet are a
usual sight in Mandaree and can be a nuisance to area residents because
of light and noise pollution. Another commenter stated that flares were
not being lit when they should have.
Response: We acknowledge the concerns expressed by the commenters
and offer a clarified explanation of the purpose and operation of the
flares being used by operators of oil and natural gas production
facilities on the FBIR.
The purpose of flaring the natural gas that is coproduced when
extracting oil from the FBIR wells is to prevent the emission of VOC
gases that might otherwise be vented to the ambient air when the
natural gas cannot be captured and injected into a sales pipeline. The
flames from the flares indicate that the VOCs are actually being
combusted. The flares should be lit at all times that co-produced
natural gas is being routed to them rather than to the sales pipeline.
In situations where production facilities are able to take advantage of
existing infrastructure and inject produced gas into a pipeline,
flaring is significantly reduced, in some cases to the point of only
occurring as a backup control measure in the event that pipeline
injections of all or part of the produced natural gas becomes
temporarily infeasible. Situations at production facilities that are
unable to route the gas to a sales pipeline and where flares are not
visibly operating may indicate the flares are not being operated
properly and gas is being vented directly to the ambient air. This FIP
has appropriate monitoring, recordkeeping, and reporting requirements
to ensure that the flares are operating properly. Further, because the
FIP intends to limit the use of flares in favor of capture and
injection of the produced natural gas into sales pipelines as soon as
practicable, secondary impacts such as noise and light pollution from
combustion of gas are expected to be reduced by the owner or operator
complying with the rule.
Comment: One commenter speculated that the level of emissions from
flares is above the allotted amount.
Response: It is unclear what is meant by the term ``allotted
amount.'' The majority of oil and natural gas production facilities
currently in operation on the FBIR do not hold any air pollution
control permits that specify any ``allotted amount'' of emissions from
the flares. Should the combustion emissions from flaring exceed the
major source permitting thresholds under PSD specified at 40 CFR 52.21,
the owner or operator would be required to obtain a PSD permit or may
opt to obtain a minor NSR permit to become synthetically minor for
purposes of PSD prior to beginning actual construction, independently
of this FIP. Either of these permits would require the installation of
control technology sufficient to ensure protection of air quality.
Comment: Several commenters stated that the EPA should eliminate
the 500 hour limitation on pit flare usage because it is inconsistent
with the Bakken Pool Guidance and unnecessary. One commenter wondered
why use of the pit flare was limited to 500 hours per year and not
something different. The commenters also asserted that only being
allowed to assume 90% VOC destruction and removal efficiency (DRE) for
pit flares already limits the amount of pit flaring that could occur
without exceeding major source thresholds. The commenters also stated
that a limitation on the use of pit flares punishes operators that
inject recovered produced natural gas and natural gas emissions into
existing pipeline infrastructure to sell it, because 98% VOC DRE
control devices are more costly. Another commenter asked who will
monitor the pit flare operations and what the repercussions are if a
source exceeds the limit of 500 hours of operation in any consecutive
12-month period?
Response: We disagree with the commenters that the 500 hour
limitation on pit flare usage is unnecessary. The purpose of the 500-
hour per year limit on use of a pit flare as a backup control device in
instances where injection of produced natural gas and natural gas
emissions is temporarily infeasible is to discourage the use of pit
flares as a primary control device. Based on past EPA guidance \17\
that addresses backup situations, we have concluded that applying a 500
hour per year limit to the oil and natural gas production facilities
for the use of a pit flare in backup situations is reasonable and
consistent with backup operation timeframes
[[Page 17845]]
allowed for other industry sectors. In addition, past EPA enforcement
settlements 18 19 that address backup situations have led us
to conclude that 500 hours (or 21 days) is a reasonable period of time
for owners and operators of oil and natural gas production facilities
to address these situations and maintain compliance with the rule.
During development of the draft synthetic minor NSR permits prior to
this rule, we had discussions with owners and operators indicating that
many oil and natural gas production facilities on the FBIR regularly
utilize temporary 98% VOC DRE control devices while they are preparing
a facility for permanent production and storage operations;\20\
therefore, we concluded it is reasonable to expect that an owner or
operator could acquire one of these temporary control devices in
situations where use of the pipeline may be infeasible for more than
500 hours.
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\17\ Memo from John S. Seitz, Director, Office of Air Quality
Planning and Standards, to Regional Air Division Directors, Regions
1-10, Calculating Potential to Emit (PTE) for Emergency Generators
(September 6, 1995), available at https://epa.gov/region07/air/title5/t5memos/emgen.pdf and included in the docket for this rule
under Docket ID: EPA-R08-OAR-2012-0479, which can be accessed at:
https://www.regulations.gov.
\18\ Consent Decree United States of America v. Marathon
Petroleum Company, LP, and Catlettsburg Refining, LLC, available at:
https://epa.gov/compliance/resources/decrees/civil/caa/marathonrefining-cd.pdf and included in the docket for this rule
under Docket ID: EPA-R08-OAR-2012-0479, which can be accessed at:
https://www.regulations.gov.
\19\ Consent Decree United States of America, and the State of
Indiana, and Plaintiff Intervenors v. BP Products North America,
Inc, available at: https://epa.gov/compliance/resources/decrees/civil/caa/whiting-cd.pdf and included in the docket for this rule
under Docket ID: EPA-R08-OAR-2012-0479, which can be accessed at:
https://www.regulations.gov.
\20\ As discussed in the preamble for the interim final rule (77
FR 48880), the EPA Region 8 air permit and enforcement programs
hosted a Fort Berthold Oil and Natural Gas Production Minor NSR
Permitting Process Meeting with the oil producers in late August
2011. Representatives from the Tribes were invited and attended in
person and by phone. Discussions included the anticipated permitting
timeline for permit applications submitted by the oil producers.
Between August 23 and September 1, 2011, a draft example synthetic
minor permit was sent by EPA to the meeting attendees and the Tribes
in preparation for the next meeting on September 1, 2011. Then, on
September 1, 2011, Region 8 hosted a permitting workshop.
Representatives from the various oil producers and the Tribes were
invited and attended. Representatives of the NDDoH also participated
by phone. The minor NSR permitting process was discussed, as well as
questions that the companies submitted ahead of time. The group
began discussions on the draft example permit and set up a workshop
specifically to delve into the specific permit conditions for the
following week. On September 7 and 8, 2011, the EPA hosted a two-day
follow-up permitting workshop. All previous meeting attendees were
invited, including the Tribes. Participants included the oil
producers and their consultants. NDDoH representatives were also on
the phone. At this meeting the group went through the draft example
permit and discussed the proposed conditions and appropriate edits.
Also discussed was what would constitute a complete application
(administrative and technical) and the various methods of PTE
calculation proposed by the companies in attendance. The EPA Region
8 hosted an additional meeting on November 30, 2011 to discuss the
revised example permit, and representatives from the various oil
producers and the Tribes were invited and attended. During these
permitting workshops, it was brought to our attention that owners
and operators routinely use temporary, portable utility flares
capable of achieving a 98% VOC DRE for the initial period when a new
oil and natural gas production facility is being prepared for
permanent operations. A copy of the attendee list for each meeting
has been included in the docket for this rule under Docket ID: EPA-
R08-OAR-2012-0479, which can be accessed at: https://www.regulations.gov.
---------------------------------------------------------------------------
The final rule requires the owners and operators to monitor and
keep records of the hours that a pit flare is operated, a description
of the justification for use and the volume of gas sent to it, to
ensure that the EPA can make a determination, if necessary, that
injection of produced natural gas and natural gas emissions into a
pipeline for sale or other beneficial purpose, or the use of the
primary control device, has been maximized. Any deviations of these
requirements must be reported to the EPA.
Comment: Several commenters stated that the EPA should clarify that
98% DRE utility flares and combustors are not required to be installed
as backup control devices if an operator chooses to route vapors to a
production line and use a 90% VOC DRE control device as backup. The
commenters stated that such a clarification would prevent operators
tied into a sales line from keeping utility flares or combustors idle
and on-site for infrequent backup use.
Response: We agree. While the rule does not require the use of
utility flares and combustors as back-up control devices if the owner
or operator is routing produced natural gas and natural gas emissions
to a sales line, the rule does not clearly state this. The rule has
been clarified.
Comment: Commenters stated that control requirements during
completions, recompletions, and for the first 90 days of production are
insufficient. The commenters urged the EPA to require that any flaring
under the FIP be performed using an enclosed vent system, along with a
utility flare or a similar device, which is capable of 98% VOC DRE.
Response: We disagree with the commenter that control requirements
during completions, recompletions, and for the first 90 days of
production are insufficient. This FIP establishes requirements to
control air pollution in the form of VOC emissions from oil and natural
gas production and storage operations on the FBIR, comparable to those
requirements developed by state permitting authorities. In other words,
we were motivated to level the playing field for the regulated
community. With that in mind, the NDIC and NDDoH allow the use of pit
flares or other 90% VOC DRE control devices during completions and
recompletions. Shared by both the State of North Dakota and the EPA,
another reason to limit the required VOC destruction efficiency to 90%
VOC DRE is that an owner or operator may be put at a significant
economic disadvantage if they purchase and install the much more
expensive 98% VOC DRE control devices and within the first 90 days
after the first date of production a well is found to be too low
producing to justify continued production and must be shut-in.
Comment: Several commenters stated that the EPA must clarify that
emissions from completion and recompletion operations do not need to be
vented to a flare until the level of VOC is sufficient to support
combustion. The commenters asserted that one might interpret the FIP
language which required each owner or operator to ``route all
casinghead natural gas to a utility flare or a pit flare capable of
reducing the mass content of VOC by at least 90%''(77 FR 48895) to
include venting materials that are not flammable and therefore unable
to sustain combustion. The commenters stated that such an
interpretation would make compliance with the rule impossible, as
vented materials are typically not flammable in the early stages of
completion or recompletion. The commenters cite ``Letter to Mr. Matthew
Todd from Peter Tsirigotis, Director, Sector Policies and Programs
Division (Sept. 28, 2012)'' as evidence that the EPA recently reached a
similar conclusion.\21\
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\21\ A copy of the letter has been included in the docket for
this rule under Docket ID: EPA-R08-OAR-2012-0479, which can be
accessed at: https://www.regulations.gov.
---------------------------------------------------------------------------
Response: While the regulatory language at Sec. 49.4164(b) in the
interim final rule is not specific on this point, the recordkeeping
requirements for well completion and recompletion operations in Sec.
49.4167(a)(4)(ii) of the interim final rule specifically require
logging the date, time, and duration of any venting of casinghead
natural gas from the oil and natural gas well; and specific reasons for
each instance of venting in lieu of capture or combustion. Therefore,
this requirement allows some degree of venting materials that may not
be flammable during well completion and recompletion operations.
Comment: Several commenters stated that this FIP is inconsistent
with NSPS OOOO and adds further confusion for operators who will be
required to comply with both sets of requirements.
[[Page 17846]]
These commenters further state that for all sources to which NSPS OOOO
applies, the FIP should mirror NSPS OOOO requirements for oil and
produced water tank control devices. Specifically, the commenters
stated that because the NSPS OOOO does not take effect for tanks for
one year, the inconsistency results in an unnecessary burden. The
commenters also asserted that since NSPS OOOO does not apply to heater-
treaters, the requirements in the FIP for heater-treaters should mirror
the requirements of the NDDoH regulations precisely. The commenter also
expressed concern that the terms of NSPS OOOO are still subject to
challenges that have not been resolved, although the commenter
indicated that the EPA was in discussions with industry representatives
to resolve those issues.
Response: We disagree that differences between this FIP and NSPS
OOOO result in an ``unnecessary burden'' to owners or operators
affected by the rules. Where there are differences between this FIP and
NSPS OOOO, NDDoH requirements, and NDIC requirements, they exist for a
specific reason. For example the requirements in this FIP for produced
oil and produced water storage tanks provide legally and practicably
enforceable control requirements for facilities currently operating on
the FBIR until applicable storage tank requirements become effective
under NSPS OOOO. At that time, the provisions in the NSPS OOOO for
produced oil and produced water storage tanks will supersede the
produced oil and produced water storage tank requirements in the FIP at
Sec. 49.4164(f), and owners or operators will never be required to
comply with both sets of requirements since duplicate requirements do
not apply to the affected equipment. In addition, we are addressing
emissions controls for heater-treaters because we determined such
controls are cost effective and have been demonstrated to be effective
in light of the air quality concerns at play in the area. Specifically,
we included the provision in the FIP at Sec. 49.4164(d)(2)(iii), which
requires aggregate storage tank VOC emissions at any facility that are
greater than 20 tpy to be reduced by at least 98%, and VOC emissions
less than 20 tpy to be controlled by at least 90%. We evaluated and
adopted this FIP provision, which is consistent with the requirements
for the heater-treaters found in the NDIC requirements at 38-08-06.4
and the heater-treater requirements in the Bakken Pool Guidance. We
acknowledge that the 98% VOC DRE control requirement for heater-
treaters in this FIP is at the upper end of the 90-98% range in the
Bakken Pool Guidance. However, the owners and operators of oil and
natural gas production facilities on the FBIR have indicated that a 98%
VOC DRE is achievable and committed in their synthetic minor NSR
applications to reduce the mass content of VOC emissions routed to the
enclosed combustors or utility flares used for both produced gas from
heater-treaters and flashing gas from storage tanks by at least 98%.
With this reduction, the owners and operators demonstrated that for
most of their facilities the potential emissions would not trigger the
requirements to obtain a PSD and/or Part 71 permit when accounting for
the requested federally enforceable restrictions. The 98% level of
control is necessary because of the high volume of VOC emissions that
must be controlled.
The commenter did not specifically state which ``challenges'' to
NSPS OOOO they were referring to in their comment. However, current
petitions filed concerning NSPS OOOO are outside of the scope of this
rule. Regardless of any future changes to NSPS OOOO, the primary intent
of FIP is to provide environmental protection on the FBIR by creating
federally enforceable control requirements for oil and natural gas
operations on the FBIR. Additionally, as discussed above, these FIP
requirements are consistent with the State's requirements.
Comment: Multiple commenters stated that completion and
recompletion requirements should be removed from the FIP because
completion and recompletion requirements in NSPS OOOO only apply to
hydraulically fractured natural gas wells, and that the application of
these activities to oil wells in the FIP is therefore inconsistent with
NSPS OOOO.
Response: This FIP requires owners or operators to route emissions
from well completion and recompletion operations to a combustion
device. This is similar to the requirements for hydraulically fractured
gas wells in NSPS OOOO prior to January 1, 2015. While requirements for
completions and recompletions in the NSPS OOOO only apply to natural
gas wells, the FIP includes this requirement for the oil and natural
gas wells on the FBIR because of the high amount of associated natural
gas in the crude oil. This is a significant source of VOC emissions
that required control in the FIP and we think such a requirement is
appropriate given the emissions characteristics of these wells in the
Bakken formation, regardless of the emissions characteristics of other
oil and natural gas production wells nationwide.
Comment: Commenter stated that the EPA should require recompleted
oil and natural gas wells on the FBIR to perform reduced emission
completions (RECs). The commenter asserted that many states including
Colorado and Wyoming currently require RECs, and that both states have
thriving oil and natural gas industries.\22\ The commenter also stated
that several natural gas companies currently employ use of RECs despite
the fact that they are not required. The commenter insisted that, if
RECs are determined not to be economical in areas like the FBIR with
limited natural gas pipeline and gathering line infrastructure, the EPA
must find alternative local uses for the natural gas. Commenter stated
that the EPA should at least require RECs on the FBIR in the near
future, similar to the NSPS. Commenter stated that the EPA's NSPS OOOO
will require RECs at all new and modified gas wells beginning in 2015.
Furthermore, another commenter stated that if the FIP were to require
green completions, advanced notice of completion or recompletion as is
included in the NSPS OOOO would be a critical requirement in the FIP.
---------------------------------------------------------------------------
\22\ Commenter cites William C. Allison, Director, Air Pollution
Control Division, Colorado Department of Public Health and the
Environment, Testimony before the United States Senate, Environment
and Public Works Committee, Clean Air and Nuclear Safety
Subcommittee, June 19, 2012. A copy of this transcript has been
included in the docket for the rule under Docket ID: EPA-R08-OAR-
2012-0479, which can be accessed at: https://www.regulations.gov.
---------------------------------------------------------------------------
Response: RECs cannot be performed if there is no gathering line
available to convey natural gas produced during the completion
flowback. Such lines are not likely to be available if the well
location has no access to a natural gas gathering system. Although
pipeline infrastructure is currently being developed on the FBIR, we do
not believe there is currently sufficient access to natural gas
gathering pipelines in all development areas of the FBIR to require
RECs at this time. We recognize the potential for VOC emissions from
well completion and recompletion operations and have maintained the
requirement in the final rule to reduce these emissions by at least
90%. If we determine at a later date that there is a need for
additional control of VOC emissions from well completion and
recompletion operations, we may propose additional FIPs or propose
supplements to this FIP.
Comment: One commenter stated that the emission control
requirements of the FIP will not exceed the current NDIC emission
control requirements,
[[Page 17847]]
providing a ``smooth transition'' for the owners or operators. Another
commenter requested more stringent emission limits be required than the
NDIC requirements. A third commenter expressed concern that the
regulations of the proposed FIP are equal to the NDDoH regulations and
noted that the FBIR is its own nation, and therefore the FIP
regulations are pertinent to the residents of the FBIR and not
individuals outside the FBIR's boundaries.
Response: One of the goals of this FIP is to provide air quality
protection for the residents of the FBIR, while also allow for
continued development of mineral resources. The FIP requirements are
consistent with the most relevant aspects of the North Dakota rules
based on our evaluation that the level of control was appropriate for
meeting these goals while ensuring the enforceability required by a
federal rule. We also evaluated over 150 synthetic minor NSR permit
applications \23\ to identify the most significant sources of VOC
emissions and associated control equipment employed by the operators to
ensure that the control requirements in this FIP are based on the
nature of oil and natural gas production and storage operations on the
FBIR.
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\23\ The information reviewed was contained in synthetic minor
NSR applications submitted to EPA, which are included in the docket
for this rule under Docket ID: EPA-R08-OAR-2012-0479, which can be
accessed at: https://www.regulations.gov.
---------------------------------------------------------------------------
Comment: Several commenters stated that the requirements of the FIP
are too stringent. The commenters also noted that since FBIR is in
attainment with all applicable NAAQS, highly stringent controls are
neither appropriate nor necessary. The commenters stated that the 98%
control required in the FIP is above the 90-98% range the EPA allowed
in recent CAFOs. The commenters also stated that the requirements of
the FIP are inconsistent with the requirements that currently apply to
operators of the same type of facilities through NDDoH regulations,
specifically the Bakken Pool Guidance. The commenters asserted that the
more burdensome requirements of the FIP as compared to those outside
the FBIR may discourage expansion of operations within the FBIR.
On the other hand, other commenters stated their support of the
EPA's requirements in the FIP, and encouraged the EPA to retain the 98%
VOC DRE requirement for flaring at storage tanks, restating the EPA's
position that this level is appropriate considering the unique
geochemistry of the Bakken formation.
Response: We disagree that the requirement to reduce VOC emissions
from production and storage operations by 98% is too stringent or
burdensome. The owners and operators of oil and natural gas production
facilities on the FBIR have indicated that a 98% VOC DRE is achievable
and have even committed to it in their synthetic minor NSR applications
to reduce the mass content of VOC emissions routed to the enclosed
combustors or utility flares used for both produced gas from heater-
treaters and flashing gas from storage tanks by that amount. The high
VOC content of the oil and natural gas produced from Bakken Pool
operations allows for a higher DRE. Many of the owners and operators of
oil and natural gas production facilities indicated that a DRE of 98%
was imperative to limit the applicability of permitting requirements
that may result if only a 90% creditable reduction of VOC emissions is
allowed. We also evaluated regulations in other oil and natural gas
producing states within Region 8 and note that this FIP is consistent
with Wyoming's requirements to control both storage tank and separation
vessels by 98%.
Comment: Multiple commenters expressed concern with the
requirements in Sec. 49.4164 which states that, beginning with the
first date of production, facilities subject to the rule are required
to route natural gas emissions from production operations and storage
operations to a 90% emissions reduction device. Within 90 days of the
first date of production, this device must be either replaced with a
98% emissions reduction device or tied to a gas sales line. The 90-day
time frame listed in the rule should be extended to at least 180 days,
to allow operators time to get the required equipment. There is added
concern that given the number of devices that may need to be purchased
for new facilities, particularly with the impending implementation of
NSPS Subpart OOOO, equipment shortages will be expected. Further,
commenters stated that the EPA should include a provision here that
allows for an extension of the 180-day time limit for upgrading to a
sales line or 98% control device in the event such equipment is
unavailable.
Response: We disagree with the commenter that we should change the
90-day timeframe allotted to either replace a 90% emissions reduction
device with a 98% emissions reduction device or inject produced natural
gas and natural gas emissions to a gas sales line. One of the goals of
this FIP is to protect human health and the environment and the
required VOC emission control should be achieved as expeditiously as
possible. Furthermore, when evaluating the estimated emissions provided
by the oil and natural gas production operators for the facilities
covered by the August 2011 CAFOs (77 FR 48879), we found that in many
cases, the difference in controlled heater-treater emissions between
only 90% VOC DRE for 90 days or less versus more than 90 days is the
difference between being a true minor source of VOC emissions under the
Federal Tribal NSR regulations and being a major source of VOC
emissions under the PSD regulations based on the high VOC emissions
from these oil and natural gas operations on the FBIR.
We recognize that some owners and operators might need time to
acquire equipment that achieves the required VOC control and we
believe, based on the information in permit applications provided by
the owners and operators on the FBIR that 90 days is a reasonable
timeframe to acquire the necessary control equipment. The interim final
FIP contains a provision that the owner or operator may use 98% VOC DRE
control devices other than those specified in the FIP upon prior
written approval from the EPA. Based on information submitted to date
by an operator requesting alternative control device approval, it is
possible to economically engineer shop-built flares that can be
demonstrated to meet the required VOC DRE and that can be used until a
utility flare becomes available, if insertion of the produced natural
gas to a sales pipeline or use of the produced natural gas for other
beneficial purpose is demonstrated to not be feasible.\24\
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\24\ A copy of the submittal from Lisa Decker, WPX Energy, to
Carl Daly, EPA Region 8 Air Program Director, on November 13, 2012
has been added to docket for the rule under Docket ID: EPA-R08-OAR-
2012-0479, which can be accessed at: https://www.regulations.gov.
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F. Monitoring and Recordkeeping Requirements
Comment: Multiple commenters stated that the EPA should impose less
burdensome monitoring and recordkeeping requirements for minor sources.
The commenters asserted that the level of detail required in the FIP is
generally required only for major sources, and that it is higher than
the detail required for minor sources by NDDoH regulations and the
Bakken Pool Guidance. The commenters stated that the FIP should mirror
NDDoH regulations regarding heater-treater control devices, meaning
that monitoring and recordkeeping requirements should be eliminated.
The commenters stated that the cost of monitoring and recordkeeping in
the
[[Page 17848]]
FIP is high compared to the benefit, and that these factors will create
a disincentive to expand drilling on the FBIR. Although one commenter
stated that the EPA's monitoring and reporting requirements are
reasonable and will facilitate compliance while also gathering
pertinent information on operations. Yet another commenter stated that
the EPA's monitoring and reporting requirements could be even more
stringent to include leak monitoring of the closed vent systems and
advanced notification prior to performing a well completion or
recompletion.
Response: We acknowledged in the Federal Register notice and the
TSD for the interim final FIP that monitoring, reporting, and
recordkeeping (MRR) requirements were an area where the FIP would
differ from the NDIC and NDDoH regulations, and the Bakken Pool
Guidance. Federal regulations must contain requirements that are
legally and practicably enforceable; and therefore this FIP contains
legally and practicably enforceable provisions that are necessary to
meet the requirements for federal regulations. Recognizing that this
FIP regulates different oil and natural gas production equipment than
NSPS OOOO, the approach we took in developing MRR requirements for oil
and natural gas production emission control equipment is similar to the
approach the Agency used in developing MRR requirements for gas well
production emission control equipment. Therefore, we do not believe the
requirements are any more burdensome than requirements for similar
equipment in NSPS OOOO.
Comment: Several commenters stated that the EPA should allow an
operator to make a visual inspection only once per quarter, and should
require that operator to conduct a one-hour Method 22 evaluation only
if the control device is actually smoking. The commenters asserted that
the amount of time it would take just to conduct quarterly monitoring
without this change could potentially require three full-time
equivalent operators for that task alone.
The commenters requested that the EPA make two additional changes
to the FIP's current requirements for monitoring smoking combustion
devices, though the commenters ultimately stated that the resource
burden to meet the smoke monitoring requirements would still be extreme
regardless of whether the two changes were made. The first change is
that the EPA increase the amount of time a control device can smoke
before being considered a ``smoking'' device from two minutes to five
minutes for consistency.\25\ The second change is that the EPA remove
the phrase ``whenever an operator is on site'' from Sec.
49.4166(g)(3). The commenter stated that this phrase is ambiguous when
read in conjunction with the phrase ``at a minimum quarterly.'' The
commenters also stated that it would be extremely burdensome for an
operator to observe a flare for an entire hour each time that operator
was on site. The commenters ultimately stated that even with this
change, the requirement would still be extremely burdensome.
---------------------------------------------------------------------------
\25\ Commenter does not list the rule with which such a change
would maintain consistency.
---------------------------------------------------------------------------
Response: We agree with the commenters that the EPA should only
require an operator to conduct a Method 22 evaluation if visible smoke
emissions are observed. We also agree with the commenter's request that
we increase the amount of time a control device can smoke before being
considered a ``smoking'' device from two minutes to five minutes. This
is consistent with the specification in NSPS OOOO at Sec.
60.5415(e)(vii)(C) and (e)(vii)(D)(3), and the general provisions at
Sec. 60.18(b) for visible emissions testing of combustion control
devices (77 FR 49556). However, we do not agree that one-hour
observations are suitable, as both Sec. 60.18(b) and NSPS OOOO require
two-hour observations and we have no reason to conclude that a
different approach is appropriate here.
We have revised the applicable condition in this final FIP to
require the owner or operator to monitor for visible smoke and to only
conduct a Method 22 evaluation if visible smoke emissions are observed.
We have also revised the provision to specify that visible smoke
emissions are present if smoke is observed more than five minutes in
any 2 consecutive hours. We have not removed the requirement to conduct
on site inspections of the operation of the device when an operator is
onsite, but not less frequently than quarterly, because we disagree
that this requirement is ambiguous. In addition, since we changed the
monitoring provision to require observations for visible smoke before
triggering the requirement for Method 22 evaluations, the commenters'
concern that the requirements are burdensome has been addressed.
Comment: Several commenters stated that the EPA should allow the
operator to make frequent onsite checks or use other alternatives to
meet the continuous recording device requirement in Sec.
49.4165(c)(6)(v) for utility flares and enclosed combustors. The
commenters asserted that there are significant challenges with
obtaining the appropriate continuous monitoring equipment, and that
operator checks should therefore be accepted as fully meeting the
requirement, or at least as meeting the requirement in the interim.
Response: We agree that there needs to be an opportunity to perform
alternative monitoring upon prior written EPA approval. We have revised
the applicable provision at Sec. 49.4166(i) to reflect this in the
final rule.
Comment: One commenter stated that the EPA should ``require
regulated entities to regularly monitor VOC emissions from the
components of closed-vent systems, using well-established methods and
leak thresholds.'' The commenter stated that in the preamble and
proposed regulatory text, the EPA required proper maintenance and
operation of vent lines, connections, fittings, valves, relief valves,
or any other appurtenance employed to contain, collect and transport
gases, and required that these components be designed to operate with
no detectable natural gas emissions (77 FR 48889, 48896). However, the
EPA failed to require producers to demonstrate or verify that the
required closed-vent systems are ``maintained and operated properly''
or ``operate with no detectable natural gas emissions.'' Commenter
stated that without a monitoring or verification requirement, the
requirements for closed-vent systems ``will be unenforceable and
largely hortatory in nature.''
Commenter also stated that the lack of monitoring or verification
requirements for closed-vent systems is at odds with the goal of the
FIP, which is to establish emission limits at oil and natural gas
facilities that are legal and practically enforceable. Commenter
asserted that absent these verification requirements, a producer could
not guarantee natural gas is controlled at 90% or 98%, and the EPA
could not guarantee that the projected emission reductions have been
achieved. Commenter stated that the EPA requires closed-vent monitoring
techniques in other regulations, including NSPS OOOO and the ``National
Uniform Emission Standards.'' \26\ Commenter recommended that, at a
minimum, the EPA use the approach proposed by the agency in the
National Uniform Emission Standards.
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\26\ ``National Uniform Emission Standards for Storage Vessel
and Transfer Operations, Equipment Leaks, and Closed Vent Systems
and Control Devices; and Revisions to the National Uniform Emission
Standards General Provisions,'' 77 FR 17,898, 17,943 and 18,009
(proposed Mar. 26, 2012) (proposed 40 CFR 65.429(a)).
---------------------------------------------------------------------------
[[Page 17849]]
Response: We disagree that leak detection and repair (LDAR)
requirements should be included in this FIP. As discussed in the
preamble and TSD for NSPS OOOO, it was determined that LDAR monitoring
was not cost effective for smaller oil and natural gas production
facilities and we have no information from which to conclude that the
same is not the case here. To demonstrate compliance with the
requirements for closed-vent systems, the final rule requires all vent
lines, connections, fittings, valves, relief valves, or any other
appurtenance on tank covers and closed-vent systems be maintained and
operated properly at all times and that they are visually inspected at
least quarterly while the equipment is operating. Further, each bypass
devices on all closed-vent systems are required to be equipped with a
flow meter to continuously monitor the volume of natural gas emissions
that are diverted from the natural gas gathering pipeline, or required
control device. The final rule requires that the owners and operators
keep records of all monitoring parameters and report instance where
construction and operation was not performed in compliance with the
requirements specified in the final rule.
G. Reporting Requirements
Comment: Commenter recommended that the EPA require a self-
certification mechanism, which would require a senior company official
to certify as to the truth, accuracy and completeness of its annual
report. Commenter suggested that the EPA draw on the example of the
NSPS OOOO in developing this mechanism.
Response: We agree that self-certification is an important
mechanism for assuring the public that the information submitted by
each facility is accurate and have added a provision in the rule
requiring owners or operators to certify as to the truth, accuracy and
completeness of the annual reports. The EPA already requires a similar
certification in the NSPS OOOO; therefore, we concluded that it is not
unreasonable to require the certification for reports submitted under
this FIP.
H. Cost Analysis
Comment: One commenter agreed with the EPA's position that the FIP
does not impose a significant cost on operators. Another commenter
noted the benefits of the FIP, specifically citing the substantial and
cost-effective VOC reductions that the EPA estimated in the FIP.
Response: We acknowledge the support of these commenters for this
FIP. We have included information regarding the cost-effectiveness of
this FIP in the TSD for the interim final rule.\27\
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\27\ The TSD includes a more detailed explanation of the cost
analysis for this FIP. It can be found in the docket for this rule,
Docket ID: EPA-R08-OAR-2012-0479, which can be accessed at: https://www.regulations.gov.
---------------------------------------------------------------------------
Comment: Commenter stated that the EPA does not address the
economic benefits of natural gas capture when estimating the costs and
benefits of the FIP. The commenter stated that ``producers are very
likely to derive substantial amounts of revenue by installing vapor
recovery units and gathering lines to route excess natural gas that is
captured by voluntary RECs and through other regulatory requirements to
reduce leaks.'' The commenter referenced an NRDC report \28\ and the
NSPS OOOO (77 FR 49534, 49537) to support this point. The commenter
also stated that the EPA noted this revenue opportunity in the FIP TSD,
though it did not address it in the FIP itself. The commenter stated
that it is especially important to consider these benefits because the
EPA notes that its analysis already overestimates costs, and also
generally stated that gas is a valuable commodity that should not be
wasted.
---------------------------------------------------------------------------
\28\ ``Natural Resources Defense Council, Leaking Profits: The
U.S. Oil and Gas Industry Can Reduce Pollution, Conserve Resources,
and Make Money by Preventing Methane Waste,'' 2012. A copy of this
document has been included in the docket for this rule under Docket
ID: EPA-R08-OAR-2012-0479, which can be accessed at: https://www.regulations.gov.
---------------------------------------------------------------------------
Response: We did not discuss the use of RECs in the cost analysis
in the TSD, as there is not currently adequate access to pipeline
gathering systems on the FBIR to require RECs from well completion and
recompletion operations, thus the current infrastructure is not
amenable to this technique at this time. However, if we determine at a
later date that there is a need for additional control of VOC emissions
during oil and natural gas production well completion and recompletion
operations on the FBIR, we may propose additional FIPs or propose
supplements to this FIP.
Comment: Commenter stated that the EPA failed to quantify the
economic benefits of protecting public health and ecosystems from
pollution in the FIP. Commenter stated that increased oil and natural
gas production leads to increased levels of ozone in the surrounding
area, risking public health.\29\ Commenter stated that the EPA must
consider the medical and other public health costs associated with oil
and natural gas production and resulting ozone in order to provide an
accurate economic impact assessment for the FIP.
---------------------------------------------------------------------------
\29\ Commenter provides several examples in which oil and gas
development drives up ozone emissions. See NRDC comments in the
docket for this rule for specific citations.
---------------------------------------------------------------------------
Response: Given the accelerated development in this area, the high
VOC emissions associated with the oil and natural gas operations and
the absence of infrastructure on the FBIR, we determined the FIP should
be effective immediately upon promulgation to ensure the protection of
public health and the environment from exposure to air pollution, avoid
fire hazards and protect the public from hazardous conditions. This FIP
establishes regulations that significantly reduce VOC emissions from
oil and natural gas production facilities on the FBIR, thereby
protecting public health and the environment. This FIP is not a
significant regulatory action under Executive Order 12866 and therefore
an analysis of the potential costs and benefits associated with this
action is not required. While we did not specifically quantify the
economic benefits of protecting public health and the environment in
the cost analysis, the control equipment required by this FIP is
already extremely cost effective at less than $15/ton, and any
additional cost benefits due to possible reduced public health costs
would only result in increased cost effectiveness. Therefore, we
believe the cost analysis sufficiently addresses the economic impacts
for this action.
I. Public Notice
Comment: A commenter stated that the EPA did not provide the public
with proper notice of the hearing, and therefore failed to ensure
public participation in the rulemaking process. The commenter stated
that the notice of the hearing in the tribal newspapers mistakenly
referred to the hearing as a ``meeting,'' which the commenter noted is
quite different than a hearing. The commenter also stated that
information about the hearing should have been advertised on the radio,
and noted that many residents in the FBIR have limited internet access.
Some commenters blamed lack of adequate notice on what they observed to
be a low turnout at the hearing(s). One commenter stated that the oil
companies had been given adequate notice, but the public had not. One
commenter urged the EPA to come back and host more hearings. Several
commenters requested an extension of the comment period, but none
specified a suggested length of extension.
Response: We disagree with these comments. We have exceeded the CAA
[[Page 17850]]
public notice requirements for rulemaking. Under Section 307, the EPA
is required to allow any person to submit written comments, data, or
documentary information, as well as give interested persons an
opportunity for the oral presentation of data, views, or arguments. The
EPA is required to keep a transcript of any oral presentations and keep
the record of the proceeding open for 30 days after completion of the
proceeding to provide an opportunity for submission of rebuttal and
supplementary information. The EPA is required to allow a reasonable
period of at least 30 days for public participation.
As explained earlier in this notice, in promulgating this rule, the
EPA is exercising its discretionary authority under sections 301(a) and
301(d)(4) of the CAA to promulgate regulations as necessary to protect
tribal air resources. Therefore, while the Title I planning
requirements of the CAA applicable to states do not directly apply to
the EPA in promulgating a FIP in Indian Country, the EPA used the
public notice requirements found within the planning requirements as a
guide in developing this FIP. For this FIP, the EPA also followed the
public hearing and public notice regulations in 40 CFR 51.102 as a
guide. According to CAA sections 301(a) and 301(d)(4) and 40 CFR
51.102, notice given to the public is to be provided by prominent
advertisement in the affected area announcing the date(s), times(s),
and place(s) of such hearings. Each proposed plan is to be made
available for public inspection in at least one location in each region
that it will apply.
The proposed FIP was published in the Federal Register on August
15, 2012. The Federal Register notice stated that public hearings would
be held on September 12, 2012 from 1-4 p.m. and again at 6-8 p.m. at
the 4 Bears Casino and Lodge in New Town, ND. An address for the
location and contact information was provided. The Federal Register
notice provided for a 60-day comment period, which required that public
comments be received by the EPA Region 8 by October 15, 2012 and
provided instructions for submitting comments. Two locations for review
of publically available supporting docket materials for this FIP were
listed including one at the EPA Region 8 office in Denver and one at
the Environmental Division office of the Three Affiliated Tribes of the
Mandan, Hidatsa, and Arikara Nation, in New Town, ND. A link for
publically available electronic docket materials was listed in the
Federal Register notice.
A public notice was posted in the following newspapers regarding
the availability of this FIP for public comment on August 15 and 17,
2012: Bismarck Tribune, Dickinson Press, Minot Daily News, New Town
News, Williston Herald, MHA Times, and Mountrail County Record. This
public notice included all of the information about the public
hearings, docket review locations (including internet link), contact
information, and the instructions for submittal of comments that was
contained in the Federal Register notice. Additionally, this public
notice listed seven locations and addresses where the public could
review copies of this FIP and all supporting docket materials in
addition to the two listed in the Federal Register notice, including:
Three Affiliated Tribes of the Mandan, Hidatsa, and Arikara Nation's
Administration Office, New Town, ND; Fort Berthold Community College
Library, New Town, ND; Mandaree Community Center, Mandaree, ND;
Parshall Segment Office, Parshall, ND; Twin Buttes Memorial Hall,
Halliday, ND; White Shield Segment Office, Roseglen, ND; and Four Bears
Community Building, Four Bears Village, ND. The EPA confirmed that this
public notice was published in each of the seven local newspapers. We
confirmed that copies of the FIP and administrative records were
received on August 13, 2012 by each of the nine locations listed above.
We also prepared a public notice and request for comment bulletin.
A copy of the bulletin was provided to the Director of the Three
Affiliated Tribes of the Mandan, Hidatsa, and Arikara Nation
Environmental Programs Office in New Town, ND on August 10, 2012 with a
request that it be posted in prominent locations throughout the
Reservation and affected area. The bulletin provided a summary of the
proposed rule, the contacts, the nine locations where the proposed rule
and administrative records could be viewed, the date, times and
location of the public hearings and referred the public to a link for
publically available electronic docket materials.
Additionally, we prepared a Public Service Announcement (PSA) for
the local radio station, KMHA 91.3 FM Radio, Fort Berthold, New Town,
ND. A copy of the PSA was provided to the Director of the Three
Affiliated Tribes of the Mandan, Hidatsa, and Arikara Nation
Environmental Programs Office in New Town, ND on August 10, 2012 with a
request that it be provided to the local radio station for broadcasting
throughout the Reservation and affected area. The PSA provided a brief
summary of the proposed rule, requested public comment through October
15, 2012, provided a contact, listed the eight locations on the FBIR
where the proposed rule and administrative records could be viewed, and
provided date, time(s) and location information for the September 12,
2012 public hearings. One of the commenters noted the PSA was aired on
the local radio station. This is documented on Page 30 of the public
hearing transcript for September 12, 2012 at 6 p.m.
Transcripts for both public hearings held on September 12, 2012
were generated and placed into the docket for this FIP. The comment
period was kept open for 30 days after the public hearing. We verified
that the seven newspaper notices published on August 15 and 17, 2012
referenced the public hearings held on September 12, 2012 as ``public
hearing'' and not as a ``public meeting.'' This included the New Town
News and the MHA Times in New Town, ND. The commenter may have intended
to refer to the PSA instead of the newspaper regarding reference to a
``public meeting'' instead of a ``public hearing.'' The PSA
inadvertently referred to the ``public hearing'' as a ``public
meeting.''
These opportunities for public participation were provided equally
to the public and the regulated community. All residents and the
regulated community were given the same opportunities to request and
access information, comment and participate in this rule making
process. Based on the Federal Register notice, newspaper notices,
posting public notice and request for comment bulletin at locations on
the reservation, holding two public hearings, making public hearing
transcripts publically available, providing a 60-day public comment
period, PSA, and links for publically available electronic docket
materials, the EPA has exceeded all legal requirements for proper
public notice of this FIP. We therefore decided not to hold additional
hearings and meetings, or extend the public comment period.
Comment: Another commenter stated that the lack of adequate public
notice was not compliant with environmental justice.
Response: We disagree with this comment. Environmental justice is
one of the Agency's highest priorities and we believe the process used
in developing this rule fully complies with the requirements of
Executive Order 12898 (59 FR 7629, February 16, 1994), which
establishes federal executive policy on environmental justice (EJ). Its
main provision directs federal agencies, to the greatest extent
practicable and
[[Page 17851]]
permitted by law, to make EJ 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 defines environmental justice as providing fair
treatment and meaningful participation in environmental decision
making. As detailed above, EPA exceeded CAA public notice requirements
for rulemaking, and the record reflects extensive efforts to ensure
meaningful participation in this case. The EPA's Action Development
Process, Interim Guidance for Considering Environmental Justice during
the Development of an Action provides additional guidance for
implementation of EO 12898 related to public notice for actions like
rulemaking. This guidance suggests inclusion of one or more public
meetings or hearings in or near affected communities and tribes. Public
meetings or hearings should include sufficient notice and should be
scheduled at a time and place convenient to the affected communities
and tribes. Successful solicitation of public comments from affected
communities and tribes may incorporate tailored outreach materials that
are concise, understandable, and readily accessible to the communities
to be reached. For remote towns and villages, local radio stations,
local newspapers, and posters at village or community centers may
represent the most effective approach. We employed these methods to
ensure that we reached the FBIR EJ community and allowed for meaningful
involvement of affected communities and tribes.
While we understand that many residents on the FBIR do not have
internet access, we employed numerous prominent advertisement methods
not relying on the internet, including newspaper notices, posting
public notice and request for comment bulletin at locations on the
FBIR, holding public hearings, providing a 60-day public comment
period, providing a PSA broadcast on local radio, as well as relying on
the internet by providing links for publically available electronic
docket materials.
We conclude that the public notice process exceeded EPA's legal
obligations in rulemakings of this type, and that there is no reason to
believe that such public notice was inadequate for compliance with the
Executive Order.\30\ Although we agree that turnout was low at the
September 12, 2012 public hearings, we do not believe that additional
public hearings or meetings would have significantly increased turnout.
We believe that low turnout at the public hearings was due to factors
other than the significant public notice methods employed. We employed
every reasonable effort to encourage attendance at public hearings and
obtain public comments on this FIP.
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\30\ See In re Shell Gulf of Mexico, Inc. & Shell Offshore,
Inc., 15 EAD ----, OCS Appeal Nos. 11-02, 11-03, 11-04, 11-08, slip
op. at 40 n. 38 (EAB Jan. 12, 2012) (treating evidence of compliance
with statutory and regulatory public participation requirements as
showing sufficiency of participation for purposes of compliance with
EO). A copy of the document has placed in the docket for this rule
under Docket ID: EPA-R08-OAR-2012-0479, which can be accessed at:
https://www.regulations.gov.
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We recognize that there are EJ concerns in the FBIR community. We
have determined that this rule will not have disproportionately high
and adverse human health or environmental effects on minority, low-
income, and indigenous populations, because it ensures compliance with
the NAAQS, which provides environmental and public health protection
for all affected populations. Compliance with the NAAQS is relevant to
an EJ claim to the extent that the NAAQS are health-based standards,
designed to protect public health with an adequate margin of safety,
including sensitive populations such as children, the elderly, and
asthmatics.
Comment: A commenter asked if the annual report of FBIR facility
activity would be accessible by the public.
Response: These reports will be submitted to the EPA Region 8
office in Denver, Colorado and maintained on file and will be available
to the public. The documents may be obtained through the Freedom of
Information Act (FOIA) process. If you seek a record, you should
address your request to the EPA Region 8 FOIA Office. Requests for
records can be sent by mail to FOIA office at Regional Freedom of
Information Officer; U.S. EPA, Region 8, Mailcode: 8-OC; 1595 Wynkoop
Street; Denver, CO 80202-1129. Request may also be made by electronic
mail to r8foia@epa.gov, by facsimile at (303) 312-6859, or by telephone
at (303) 312-6856. Your request should be as specific as possible with
regard to the subject, time frames, and locations. You do not have to
give a requested record's name or title, but the more specific you are;
the more likely it will be that the record you seek can be located. For
example, if you are seeking records dealing with the FIP annual
reports, request the FBIR FIP Annual Reports, the owner or operator you
seek information on, and the calendar year(s) for the reports you seek.
V. Summary of Final Rule and Significant Changes from the Proposed and
Interim Final Rule
A. Administrative Edits
Correction: In the proposed rule we identified incorrect citations
to the Code of Federal Regulations (CFR) for publishing the rule. The
final rule has been promulgated at Subpart K of 40 CFR part 49 which is
specific to Region 8 FIPs.
Sec. 49.140 is now Sec. 49.4161;
Sec. 49.141 is now Sec. 49.4162;
Sec. 49.142 is now Sec. 49.4163;
Sec. 49.143 is now Sec. 49.4164;
Sec. 49.144 is now Sec. 49.4165;
Sec. 49.145 is now Sec. 49.4166;
Sec. 49.146 is now Sec. 49.4167; and
Sec. 49.147 is now Sec. 49.4168.
B. Introduction
This rule applies to any person who owns or operates an existing
(constructed or modified on or after August 12, 2007), new, or modified
oil and natural gas production facility \31\ that is located on the
FBIR and producing from the Bakken Pool with one or more oil and
natural gas wells, any one of which a well completion or recompletion
operation is/was initiated on or after August 12, 2007.
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\31\ For the purposes of this rule, an oil and natural gas
production facility consists of one or more oil and natural gas
wells and the air pollution emitting units that are utilized for
production operations and storage operations for those wells. This
definition was clarified from what was proposed in the interim final
rule. Additionally, August 12, 2007 is the earliest well completion
date identified in the CAFOs.
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For the purposes of this rule, a well completion means the process
that allows for the flowback of oil and natural gas from newly drilled
wells to expel drilling and reservoir fluids and tests the reservoir
flow characteristics, which may vent produced hydrocarbons to the
atmosphere via an open pit or tank. A well completion operation means
any oil and natural gas well completion with hydraulic fracturing
occurring at an oil and natural gas production facility. The completion
date is considered the date that construction at an oil and natural gas
production facility has commenced. The recompletion date is considered
the date that a modification has occurred at an oil and natural gas
production facility. The reason we selected the initiation of
completions operations as the date for defining a new facility is that
owners and operators use drill rigs prior to
[[Page 17852]]
initial completion operations and this equipment is generally not in
one location long enough to be considered a stationary source. In
addition, it is not certain during the drilling operations whether a
well will be a producing well. Hence, it is not known whether an oil
and natural gas production facility will be constructed to support that
well. The outcome of a completion operation provides the well owners
and operators information necessary to determine whether an oil and
natural gas production facility will be constructed.
Clarification: We have added language to the introduction at Sec.
49.4161(b) to clarify that, for the purposes of this rule, the
initiation of well completion operations and well recompletion
operations are the dates that construction and modifications commence,
as set forth in the regulatory text of this final rule.
Compliance with the rule is required no later than June 20, 2013 or
upon initiation of well completion or recompletion operations,
whichever is later. Upon signature by the Administrator, we will post
this rule on our internet site (https://www.epa.gov/region8/air/fbirfip.html) and notify the owners and operators and the Three
Affiliated Tribes of the Mandan, Hidatsa, and Arikara Nation.
Clarification: We have changed the language in the introduction at
Sec. 49.4161(c) to clarify that the compliance date is upon initiation
of well completion operations and well recompletion operations, as
follows: ``Sec. 49.4161(c) When must I comply with Sec. Sec. 49.4161
through 49.4168? Compliance with Sec. Sec. 49.4161 through 49.4168 is
required no later than June 20, 2013 or upon initiation of well
completion operations or well recompletion operations, whichever is
later.''
C. Provisions for Delegation of Administration to the Three Affiliated
Tribes of the Mandan, Hidatsa, and Arikara Nation
The provisions in Sec. 49.4162 establish the steps by which the
Three Affiliated Tribes of the Mandan, Hidatsa, and Arikara Nation may
request delegation to assist us with the administration of this rule
and the process by which the Regional Administrator of the EPA Region 8
may delegate to the Tribes the authority to assist with such
administration of this rule. As described in the regulatory provisions,
any such delegation will be accomplished through a delegation of
authority agreement between the Regional Administrator and the Three
Affiliated Tribes of the Mandan, Hidatsa, and Arikara Nation. This
section provides for administrative delegation of this federal rule and
does not affect the eligibility criteria under CAA section 301(d) and
40 CFR 49.6 for TAS should the Tribes decide to seek such treatment for
the purpose of administering their own EPA-approved program under
tribal law. Administrative delegation is a separate process from TAS
under the TAR. Under the TAR, Indian tribes seek EPA-approval of their
eligibility to run CAA programs under their own laws. The Three
Affiliated Tribes of the Mandan, Hidatsa, and Arikara Nation would not
need to seek TAS under the TAR for purposes of requesting to assist us
with administration of this rule through a delegation of authority
agreement. In the event such an agreement is reached, the rule would
continue to operate under federal authority throughout the FBIR, and
the Tribes would assist us with administration of the rule to the
extent specified in the agreement.
D. General Provisions
The provisions in Sec. 49.4163 General Provisions provide: (1)
Definitions that apply to this rule; (2) assurance that we will
maintain its authority to require testing, monitoring, recordkeeping,
and reporting in addition to that already required by an applicable
requirement, in a permit to construct or permit to operate in order to
ensure compliance; and (3) assurance that nothing in the rule will
preclude the use, including the exclusive use, of any credible evidence
or information, relevant to whether a facility would have been in
compliance with applicable requirements if the appropriate performance
or compliance test had been performed.
E. Construction and Operational Control Measures
The provisions in Sec. 49.4164 Construction and Operational
Control Measures provide requirements to reduce VOC emissions during
well completion and recompletion operations. The owner or operator must
route all casinghead natural gas emissions associated with completion
and recompletion operations to a utility flare or a pit flare capable
of reducing the mass content of VOCs in the natural gas vented to it by
at least 90.0%. We note that the well completion and recompletion
control requirements to use pit flares or utility flares that have the
capability to reduce the mass content of VOC in the natural gas
emissions routed to them by at least 90.0% percent by weight are the
minimum level of control that will be allowed under this rule. Owners
and operators may also choose to perform reduced emission completions
and recompletions \32\, which would exceed the 90.0% VOC emission
reduction requirement. This section also requires the control of
production and storage operations and imposes a timeline for
installation of the controls on these operations. The owner or operator
is required to reduce the mass content of VOC emissions from natural
gas during oil and natural gas production and storage operations by at
least 90.0% percent on the first date of production.
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\32\ U.S. Environmental Protection Agency. Lessons Learned from
Natural Gas STAR Partners: Reduced Emissions Completions for
Hydraulically Fractured Natural Gas Wells. Office of Air and
Radiation: Natural Gas Star Program. Washington, DC. Available at:
https://epa.gov/gasstar/documents/reduced_emissions_completions.pdf. Accessed July 26, 2012. A copy of this document has
been placed in the docket for this rule under Docket ID: EPA-R08-
OAR-2012-0479, which can be accessed at: https://www.regulations.gov.
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Within 90 days of the first date of production, we require the
owner or operator to route the natural gas from the production and
storage operations through a closed-vent system to a utility flare or
equivalent combustion device capable of reducing the mass content of
VOC in the natural gas vented to the device by at least 98.0%. The
owner or operator also has the option to design their production and
storage operations to recover the natural gas as product and inject it
into a natural gas gathering pipeline system for sale or other
beneficial purpose. For those owners or operators that choose to
capture the natural gas as product rather than a pollutant to be
controlled, the natural gas may temporarily be routed through a closed-
vent system to an enclosed combustor, utility flare or pit flare in
instances where injection of the product into the pipeline is
temporarily infeasible. In these situations, the pit flare is
considered a backup standby unit used for unplanned flare events, such
as during temporarily limited pipeline capacity, that are beyond a
producer's control and the pit flare is used to safely burn the natural
gas product that could otherwise pose a potential risk to workers, the
community, or the environment. The owner or operator, however, must
limit the use of the pit flare in these instances to 500 hours in any
consecutive 12-month period.
The rule requires the owner or operator to route all standing,
working, breathing and flashing losses from the produced oil storage
tanks and any produced water storage tanks interconnected with the
produced oil storage tanks through a closed vent system to either an
operating system
[[Page 17853]]
designed to recover and inject the natural gas emissions into a natural
gas gathering pipeline system for sale or other beneficial use, or to
an enclosed combustor or utility flare capable of reducing the mass
content of VOC in the natural gas emissions vented to the device by at
least 98.0%. However, to prevent duplicative federal requirements for
owners and operators of storage tanks on the FBIR subject to both this
rule and NSPS OOOO, storage tanks subject to and controlled under the
requirements specified in 40 CFR part 60, subpart OOOO are considered
to meet the storage tank control requirements of this rule. No further
requirements apply for such storage tanks under this rule. In addition,
the rule provides that if the uncontrolled PTE of VOCs from the
aggregate of all produced oil storage tanks and produced water storage
tanks interconnected with produced oil storage tanks at an oil and
natural gas production facility is less than, and reasonably expected
to remain below, 20 tons in any consecutive 12-month period, then the
owner or operator may use a utility flare or enclosed combustor that is
capable of reducing the mass content of VOC in the natural gas
emissions vented to the device by only 90.0% upon prior written
approval by the EPA.\33\
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\33\ If the owner or operator receives written approval for a
new method from the EPA, the owner or operator must calculate
potential to emit based on the new EPA-approved method.
---------------------------------------------------------------------------
The control devices must be operated under specific conditions as
specified in Sec. 49.4165 Control Equipment Requirements and Sec.
49.4166 Monitoring Requirements.
F. Control Equipment Requirements
The provisions in Sec. 49.4165 Control Equipment Requirements
require the use of covers on all produced oil and water storage tanks
and the use of closed-vent systems with all VOC capture and control
equipment. Section 49.4165 also specifies construction and operational
requirements for the covers and closed-vent systems. In addition, Sec.
49.4165 requires specific construction and operational requirements of
pit flares, enclosed combustors, and utility flares.
The provisions in Sec. 49.4165 require that each owner and
operator equip the openings on each produced oil storage tank and each
produced water storage tank that is interconnected with produced oil
storage tanks with a cover that ensures that natural gas emissions are
efficiently routed through a closed-vent system to a vapor recovery
system an enclosed combustor, or a utility flare. Each cover and all
openings on the cover (e.g., access hatches, sampling ports, and gauge
wells) must form a continuous barrier over the entire surface area of
the produced oil and produced water in the storage tank. Each cover
opening must be secured in a closed, sealed position (e.g., covered by
a gasketed lid or cap) whenever material is in the tank on which the
cover is installed except during those times when it is necessary to
use an opening as follows: (1) To add material to, or remove material
from the unit (this includes openings necessary to equalize or balance
the internal pressure of the unit following changes in the level of the
material in the unit); or (2) to inspect or sample the material in the
unit; or to inspect, maintain, repair, or replace equipment located
inside the unit.
Each owner and operator is required to use closed-vent systems to
collect and route natural gas emissions to the respective VOC control
devices. All vent lines, connections, fittings, valves, relief valves,
or any other appurtenance employed to contain and collect gases, and
transport them to the VOC control equipment must be maintained and
operated properly during any time the control equipment is operating
and must be designed to operate with no detectable natural gas
emissions. If a closed-vent system contains one or more bypass devices
that could be used to divert all or a portion of the natural gas from
entering the VOC control devices, the owner or operator must meet one
of the following options for each bypass device: (1) At the inlet to
the bypass device properly install, calibrate, maintain, and operate a
natural gas flow indicator capable of taking periodic readings and
sounding an alarm when the bypass device is open such that the natural
gas is being, or could be, diverted away from the control device and
into the atmosphere; or (2) secure the bypass device valve in the non-
diverting position using a car-seal or a lock-and-key type
configuration.
Each owner or operator is required to follow the manufacturer's
written operating instructions, procedures and maintenance schedule to
ensure good air pollution control practices for minimizing emissions
from each enclosed combustor or utility flare. Each enclosed combustor
must have the capacity to reduce the mass content of the VOC in the
natural gas routed to it by at least 98.0% for the minimum and maximum
natural gas volumetric flow rate and British Thermal Unit (BTU) content
routed to it. For the purposes of this rule, we require that all
utility flares installed per this rule meet the requirements in 40 CFR
60.18(b), and all enclosed combustors installed per this rule must be
tested according to the NSPS OOOO performance testing requirements.
Until such time that compliance is required with the storage vessel
requirements in the NSPS OOOO standard, however, the owner or operators
can demonstrate compliance using methods specified in this rule.
We determined that certain work practice and operational
requirements are also necessary for the practical enforceability of the
VOC emission reduction requirement that the enclosed combustors or
utility flares must achieve. Flares and combustors must be operated
within specific parameters to effectively destroy VOC emissions.
Therefore, each owner or operator must ensure that each enclosed
combustor or utility flare is: (1) Operated at all times that produced
natural gas and natural gas emissions are routed to it; (2) operated
with a liquid knock-out system to collect any condensable vapors (to
prevent liquids from going through the control device); (3) equipped
with a flash-back flame arrestor; (4) equipped with a continuous
burning pilot flame or an electronically controlled electronically
controlled automatic igniter system; (5) equipped with a monitoring
system for continuous recording of the parameters that indicate proper
operation of each enclosed combustor, utility flare, continuous burning
pilot flame and electronically controlled automatic igniter, such as a
chart recorder, data logger, or similar devices; (6) maintained in a
leak free condition; and (7) operated with no visible smoke emissions.
Section 49.4165 requires that each owner or operator limit the use
of pit flares to: (1) The control natural gas emissions during well
completion operations; (2) the control of VOC emissions in the event
the natural gas that is being recovered for sale or other beneficial
purpose must be diverted to a backup control device because injection
into the pipeline is temporarily infeasible and there is no operational
enclosed combustor or utility flare at the oil and natural gas
production facility, in which instances the owner or operator must
limit use of the pit flare to no more than 500 hours in any consecutive
12-month period; or (3) use when total uncontrolled PTE of VOCs from
all produced oil storage tanks and any produced water storage tanks
interconnected with produced oil storage tanks at an oil and natural
gas production facility have declined to less than, and are reasonably
expected to stay below, 20 tons in any consecutive
[[Page 17854]]
12-month period. Each pit flare must be operated to reduce the mass
content of VOC in the natural gas routed to it by at least 90.0% and
must be operated with no visible smoke emissions. Each pit flare must
be equipped with an electronically controlled automatic igniter with
malfunction alarm and remote notification system if the pilot flame
fails. Each pit flare must be visually inspected for the presence of a
pilot flame any time natural gas is being routed to it and if the pilot
flame fails, it must be relit as soon as safely possible and the
electronically controlled automatic igniter must be repaired or
replaced before the pit flare is used again.
Section 49.4165 allows owners or operators of oil and natural gas
production facilities to use control devices other than an enclosed
combustor or utility flare, provided they are capable of achieving at
least a 98.0% VOC destruction efficiency and upon our prior written
approval by the EPA. This provision will allow for owner or operators
to take advantage of technological advances in VOC emission control for
the oil and natural gas production industry and will provide us with
valuable information on any new control technologies.
Deletion: We have deleted the testing requirement at Sec.
49.4165(c)(5)(iii). This was a temporary enclosed combustor testing
requirement that applied until 40 CFR part 60 subpart OOOO-New Source
Performance Standard for Oil and Natural Gas Sector (NSPS OOOO) was
promulgated. Since NSPS OOOO was promulgated on August 16, 2012 and
became effective on October 15, 2012, this temporary provision is no
longer necessary.
Correction: We have clarified control equipment requirements at
Sec. 49.4165(c)(4). We have added language at Sec. 49.4165(c)(4) to
provide an exemption to Sec. 60.18(c)(2) and (f)(2) for those utility
flares operated with an electronically controlled automatic igniter as
set forth in the regulatory text of this final rule.
Clarification: We have clarified that enclosed combustors and
utility flares must be operated properly at all times that produced
natural gas and/or natural gas emissions are routed to them, rather
than just the term natural gas. The rule now reads as set forth in the
regulatory text of this final rule at Sec. 49.4165(c)(6)(i).
Correction: We have removed the requirement to install equipment
for the monitoring of continuous burning pilot flames and
electronically controlled automatic igniters on flares and combustors.
These requirements were already provided for at Sec. 49.4166(g)(1).
The rule now reads as set forth in the regulatory text of this final
rule at Sec. 49.4165(c)(6)(iv).
Clarification: We have clarified the purpose for equipping utility
flares and enclosed combustors with a monitoring system. We have
revised the applicable provisions to read as set forth in the
regulatory text of this final rule at Sec. 49.4165(c)(6)(v).
Correction: We removed the requirement to monitor a pilot flame on
pit flares since these flares are to be operated with electronically
controlled automatic igniters only. The rule now reads as set forth in
the regulatory text of this final rule at Sec. 49.4165((d)(3(iv) and
(v).
G. Monitoring Requirements
Section 49.4166 Monitoring Requirements requires each owner or
operator conduct certain monitoring that we determined is necessary for
the practical enforceability of the VOC emission reduction
requirements, including but not limited to: (1) Monitoring of the
number of barrels of oil produced at the facility each time the oil is
unloaded from the produced oil storage tanks; (2) Monitoring of the
hours of operation of each pit flare used to control VOC emissions in
the event the natural gas that is being recovered for sale or other
beneficial purpose must be diverted to a backup control device because
injection into the pipeline is temporarily infeasible and there is no
operational enclosed combustor or utility flare is at the oil and
natural gas production facility; (3) Monitoring of the volume of
produced natural gas from the heater-treater sent to each enclosed
combustor, utility flare, and pit flare at all times; (4) Monitoring of
the volume of standing, working, breathing, and flashing losses from
the produced oil and produced water storage tanks sent to each vapor
recovery system, enclosed combustor, utility flare, and pit flare at
all times; (5) Visually inspecting storage tank thief hatches, covers,
seals, PRVs, and closed-vent systems to insure proper condition and
functioning; (6) Directly and continuously measuring, various
parameters (i.e., product throughput, enclosed combustor flame
presence, temperature, etc.) related to the proper operation of
emissions units and required control devices to assure compliance with
the emissions reduction requirements and operational limitations; and
(7) Visually inspect all equipment associated with each enclosed
combustor, utility flare, and pit flare at a minimum quarterly to
ensure system integrity; (8) Visually monitoring for visible smoke from
enclosed combustors, utility flares, and pit flares during operation.
The monitoring, recordkeeping and reporting requirements for the
covers, close-vent systems, pit flares, enclosed combustors, and
utility flares are intended to provide legal and practicable
enforceability of the emission control requirements.
Correction: We have added monitoring requirements at Sec.
49.4166(d) to describe acceptable gas volume measurement methods, thus
making this provision consistent with the provision at Sec.
49.4166(c). The rule now reads as set forth in the regulatory text of
this final rule.
Revision: We have included more flexibility in the options for
monitoring approaches. We have revised the applicable provisions to
read as set forth in the regulatory text of this final rule at Sec.
49.4166(g)(1).
Revision: We have clarified the intent of the provision at Sec.
49.4166(g)(2) in the final FIP to read as set forth in the regulatory
text of this final rule:
Revision: We have revised the smoke monitoring provisions at Sec.
49.4166(g)(3) in the final FIP to read as set forth in the regulatory
text of this final rule.
Revision: We have added a new monitoring provision at Sec.
49.4166(i) to allow for other monitoring options upon prior written
approval by the EPA, as set forth in the regulatory text of this final
rule.
H. Recordkeeping Requirements
Section 49.4167 Recordkeeping Requirements requires that each owner
or operator of an oil and natural gas production facility keep specific
records to be made available upon our request, in lieu of voluminous
reporting requirements. The records that must be kept include, but are
not limited to, all required measurements, monitoring, and deviations
or exceedances of rule requirements and corrective actions taken, as
well as any manufacturer specifications and guarantees or engineering
analyses. These recordkeeping requirements provide legal and practical
enforceability to the control and emission reduction requirements of
this rule.
Clarification: We have clarified the recordkeeping requirements at
Sec. 49.4167(a)(4)(ii) to correctly identify that casing head gas
vented from producing wells should be monitored, not produced natural
gas. The rule now reads as set forth in the regulatory text of this
final rule.
Revision: We have revised the recordkeeping requirements at Sec.
49.4167(a)(8) to clarify that records
[[Page 17855]]
must be maintained of the volume of natural gas emissions released when
close-vent systems and control devices have been bypassed or were not
operating. The rule now reads as set forth in the regulatory text of
this final rule.
Correction: We have corrected the recordkeeping requirements at
49.4167(a)(5)(iv) to include the requirement to keep records of any
instance in which an electronically controlled automatic igniter has
failed. The rule now reads as set forth in the regulatory text of this
final rule.
I. Reporting Requirements
Section 49.4168 Notification and Reporting Requirements requires
that each owner or operator of an oil and natural gas production
facility prepare and submit an annual report, beginning one year after
this rule becomes effective covering the period for the previous
calendar year. The report must include a summary of required records
identifying each oil and natural gas production well completion or
recompletion operation for each facility conducted during the reporting
period, an identification of the first date of production for each oil
and natural gas production well at each facility that commenced
operation during the reporting period, and a summary of deviations or
exceedances of any requirements of this FIP and the corrective measures
taken. Additionally, a report must be submitted for any performance
test we require.
Clarification: Upon further review of the language at Sec.
49.4168(b) regarding annual reporting requirements, we determined it
was necessary to clarify the requirement based on our original intent.
The provision now reads as set forth in the regulatory text of this
final rule:
We decided not to require owners or operators to register their oil
and natural gas production facilities, because the Federal Tribal NSR
Rule at 40 CFR 49.151 already requires registration of existing minor
sources and such a requirement in this rule would be redundant.
These reporting requirements are part of providing legal and
practical enforceability to the control and emission reduction
requirements of this rule.
Revision: As explained in the response to comments above, we have
added a provision for notification and reporting requirements at Sec.
49.4168(b)(4)(iv) requiring owners or operators to certify as to the
truth, accuracy and completeness of the annual reports. The new
provision is consistent with the NSPS OOOO (40 CFR 60.5420(b)(1)(iv))
and reads as set forth in the regulatory text of this final rule.
J. Effect on Permitting of Facilities
This rule is not a permitting program. It does not impose or exempt
the facilities from any federal CAA permitting requirements, including
the PSD preconstruction permitting requirements at 40 CFR 52.21,
Federal Tribal NSR Rule permitting requirements for minor sources at 40
CFR 49.151, or federal Title V operating permit requirements at 40 CFR
part 71. The primary purpose of this rule is to address potential
impacts to the public health and the environment. However, the rule
does provide legal and practical enforceability for the use of VOC
emission controls that are already being used voluntarily by the
industry and for VOC emissions reductions from those controls. Provided
that the facilities are in compliance with the new rule, they may take
into account the enforceable VOC emission reductions from the required
controls they use when calculating their PTE for determining
applicability of the federal permitting requirements, to the extent
that the effect those controls would have on VOC emissions is legally
and practicably enforceable.
Regardless of this rule, due to the high amount of associated
natural gas in the crude oil and the absence of infrastructure to
collect the natural gas on the FBIR, some FBIR facilities' PTE of VOCs
or any other pollutant subject to regulation may exceed the
applicability thresholds for PSD, Federal Tribal NSR Rule, or Title V
permitting even after accounting for the legally and practicably
enforceable emission reductions provided in this rule. In such cases,
the owners or operators of these facilities are required to apply for
and obtain the appropriate permits in accordance with the regulation.
K. Registration Requirements
This rule does not exempt facilities located on the FBIR from the
registration requirements of the Federal Tribal NSR Rule, promulgated
on July 1, 2011. Nor does this rule impose any additional registration
requirements. The primary purpose of this rule is to address potential
impacts to the public health and the environment. Provided that the
facilities are in compliance with the provisions of this rule,
facilities may include the enforceable VOC emission reductions
resulting from the controls required in this rule when calculating
their PTE, to the extent that the effect those controls would have on
VOC emissions is legally and practicably enforceable.
If the PTE VOCs or any other regulated NSR pollutant is less than
the major source thresholds in 40 CFR 52.21, but equal to or greater
than the thresholds in the Federal Tribal NSR Rule, then registration
is required of these facilities (40 CFR 49.160). Those facilities that
must obtain a PSD permit pursuant to 40 CFR 52.21 or wish to obtain a
preconstruction permit pursuant to 40 CFR 49.151 of the Federal Tribal
NSR Rule, in addition to meeting the requirements of this rule, are
exempt from this registration requirement.
VII. Statutory and Executive Order
A. Executive Order 12866: Regulatory Planning and Review and Executive
Order 13563: Improving Regulation and Regulatory Review
This action is not a ``significant regulatory action'' under the
terms of Executive Order 12866 (58 FR 51735, October 4, 1993) and is
therefore not subject to review under Executive Orders 12866 and 13563
(76 FR 3821, January 21, 2011).
B. Paperwork Reduction Act
The information collection requirements in this 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. An
Information Collection Request (ICR) document has been prepared by us,
and a copy is available in the docket for this action. The information
collection requirements are not enforceable until OMB approves them.
The ICR document prepared by us has been assigned the EPA ICR tracking
number 2478.01.
The information requirements are based on notification,
recordkeeping and reporting requirements in this FIP (40 CFR part 49,
subpart K). These requirements are mandatory for each owner or operator
(1) Located on the Fort Berthold Indian Reservation; (2) constructing
or operating an oil or natural gas production facility producing from
the Bakken Pool with one or more oil and natural gas wells and (3) for
which completion or recompletion operations are/were performed on or
after August 12, 2007. See 40 CFR 49.4161. These records and reports
are necessary for the EPA Administrator (or the tribal agency if
delegated), for example, to: (1) Confirm compliance status of
stationary sources; (2) identify any stationary sources not subject to
the requirements and identify
[[Page 17856]]
stationary sources subject to the regulations; and (3) ensure that the
stationary source control requirements are being achieved. The
information would be used by the EPA or tribal enforcement personnel
to: (1) Indentify stationary sources subject to the rules; (2) ensure
that appropriate control technology is being properly applied; and (3)
ensure that the emission control devices are being properly operated
and maintained on a continuous basis. Based on the reported
information, the EPA Administrator (or the delegated tribe) can decide
which stationary sources, records or processes should be inspected.
Specifically, this FIP requires that each owner or operator conduct
certain monitoring that we determined is necessary for the practical
enforceability of the VOC emission reduction requirements. See 40 CFR
49.4166. The recordkeeping requirements in 40 CFR 49.4167 require that
each owner or operator keep specific records to be made available at
the EPA's request. The recordkeeping requirements require only the
specific information needed to determine compliance. Finally, the rules
contain reporting requirements in 40 CFR 49.4168 that require each
owner or operator to prepare and submit an annual report. These
recordkeeping and reporting requirements are specifically authorized by
CAA section 114 (42 U.S.C. 7414). We believe these information
collection requirements are appropriate because they will enable us to
develop and maintain accurate records of air pollution sources and
their emissions, will provide the necessary legal and practical
enforceability, and will ensure appropriate records are available to
verify compliance with this FIP. All information submitted to us
pursuant to the recordkeeping and reporting requirements for which a
claim of confidentiality is made is safeguarded according to the Agency
policies set forth in 40 CFR part 2, subpart B.
It is estimated that 780 oil and natural gas production facilities
will be subject to this FIP over the next three years. The oil and
natural gas production facilities subject to this rule will incur
approximately 29,655 hours in annual monitoring, reporting, and
recordkeeping burden (averaged over the first three years after the
effective date of the rule), incurring an estimated $6.5 million
($2012) in burden. This includes an annual average of 29,655 labor
hours per year at a total labor cost of $1.4 million per year, average
annualized capital costs of $2.2 million per year, average annual
operating and maintenance costs of $2.9 million per year, and an
average annual estimate of 623 likely respondents over the next three
years. This estimate includes the testing requirements, emission
reports, developing a monitoring plan, notifications and recordkeeping.
All burden estimates are in 2012 calendar year dollars and represent
the most cost-effective monitoring approach for affected facilities.
Burden is defined at 5 CFR 1320.3(b).
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 our
regulations in 40 CFR are listed in 40 CFR part 9. When this ICR is
approved by OMB, we 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 this final
rule.
To assist members of the public who would like to provide comments
on the ICR, our need for this information, the accuracy of the provided
burden estimates, and any suggested methods for minimizing respondent
burden, we established a public docket for this rule, which includes
this ICR, under Docket ID: EPA-R08-OAR-2012-0479. Submit any comments
related to the ICR to the EPA and OMB. See ADDRESSES section at the
beginning of this notice for information on submitting comments to the
EPA. 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 March 22, 2013, please attempt to send comments to OMB by April
22, 2013. Before finalizing the information collection requirements, we
will respond to any comments submitted to the EPA or OMB.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act (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 this rule on small
entities, small entity is defined as: (1) A small business as defined
by the Small Business Administration's (SBA) 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.
After considering the economic impacts of this final rule on small
entities, I certify that this action will not have a significant
economic impact on a substantial number of small entities. In
determining whether a rule has a significant economic impact on a
substantial number of small entities, the impact of concern is any
significant adverse economic impact on small entities, since the
primary purpose of the regulatory flexibility analyses is to identify
and address regulatory alternatives ``which minimize any significant
economic impact of the rule on small entities'' (5 U.S.C. 603 and 604).
Thus, an agency may certify that a rule will not have a significant
economic impact on a substantial number of small entities if the rule
relieves regulatory burden, or otherwise has a positive economic effect
on all of the small entities subject to the rule.
This rule will not have a significant economic impact on a
substantial number of small entities due to the reduced regulatory
requirement, and thus the regulatory burden, to obtain federal CAA
permits that this rule provides.
D. Unfunded Mandates Reform Act (UMRA)
This 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.
As discussed in the TSD and preamble for the interim final rule, we
determined the maximum annual cost of compliance with this rule on the
oil and natural gas industry is estimated to be approximately $50
million. However, we believe this is a conservative estimate and that
actual annual costs would be much lower due to factors such as
increased facility well density, standard industry practice to use VOC
control equipment, and anticipated pipeline infrastructure development,
which is explained further in the TSD. Thus, this rule is not subject
to the requirements of sections 202 or 205 of UMRA.
This rule does not contain a significant federal intergovernmental
[[Page 17857]]
mandate as described by section 203 of UMRA. Therefore, this 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.
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 rule regulates under the CAA
certain stationary sources in Indian country that are not subject to
approved CAA programs of the State of North Dakota. Thus, Executive
Order 13132 does not apply to this action. Although section 6 of
Executive Order 13132 does not apply to this action, we consulted with
the Three Affiliated Tribes of the Mandan, Hidatsa, and Arikara Nation
in developing this action. A summary of the consultation is provided
below in section F of this preamble. In the spirit of Executive Order
13132, and consistent with EPA policy to promote communications between
EPA and State and local governments, EPA specifically solicited comment
on the 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'' (65 FR 67249, November 6, 2000),
requires us to develop an accountable process to ensure ``meaningful
and timely input by tribal officials in the development of regulatory
policies that have tribal implications.'' ``Policies that have tribal
implications'' is defined in the Executive Order to include regulations
that have ``substantial direct effects on one or more Indian tribes, on
the relationship between the Federal Government and the Indian tribes,
or on the distribution of power and responsibilities between the
Federal Government and Indian tribes.''
Under Section 5(b) of Executive Order 13175, we may not issue a
regulation that has tribal implications, that imposes substantial
direct compliance costs, and that is not required by statute, unless
the Federal Government provides the funds necessary to pay the direct
compliance costs incurred by tribal governments, or we consult with
tribal officials early in the process of developing the proposed
regulation. Under Section 5(c) of Executive Order 13175, we may not
issue a regulation that has tribal implications and that preempts
tribal law, unless the Agency consults with tribal officials early in
the process of developing the proposed regulation.
We concluded that this final rule will have tribal implications.
However, it will neither impose substantial direct compliance costs on
tribal governments, nor preempt tribal law. These regulations would
affect the FBIR community by establishing air quality regulations and
thus creating a level of air quality protection not previously provided
under the CAA. The regulatory approach used in this rule would create
federal requirements similar to those that are already in place areas
adjacent to the Reservation. Finally, although tribal governments are
encouraged to partner with us on the implementation of these
regulations, they are not required to do so. Since this final rule will
neither impose substantial direct compliance costs on tribal
governments, nor preempt tribal law, the requirements of Sections 5(b)
and 5(c) of the Executive Order do not apply to this rule.
Consistent with EPA policy, the EPA consulted with tribal officials
and representatives of the Three Affiliated Tribes of the Mandan,
Hidatsa and Arikara Nation early in the process of developing this
regulation to permit them to have meaningful and timely input into its
development.
Tribal consultation with the Three Affiliated Tribes of the Mandan,
Hidatsa, and Arikara Nation was first initiated on February 17, 2012
when we mailed a letter inviting the Tribes to consult on the first
group of synthetic minor NSR permits being issued on the Reservation
under the Federal Tribal NSR Rule. Then, on March 29, 2012, EPA senior
management and the Chairman of the Three Affiliated Tribes of the
Mandan, Hidatsa, and Arikara Nation along with other government
officials met via conference call to discuss the proposed FIP to be
developed for the FBIR. We formally invited the Tribes to consult about
this FIP in a letter dated April 10, 2012 to Chairman Tex Hall, of the
Three Affiliated Tribes of the Mandan, Hidatsa, and Arikara Nation
Council.
We again met with members of the Three Affiliated Tribes of the
Mandan, Hidatsa, and Arikara Nation Council on June 13, 2012 in New
Town to consult and receive input from the Tribes as we developed this
FIP. In attendance from the Council were the vice Chairman and two
council members. The Tribes' legal counsel was also in attendance. The
purpose of the consultation was twofold: (1) Update the Tribes on the
EPA's efforts to develop this FIP so that the air quality on the FBIR
is protected and oil and natural gas development continues; and (2)
discuss the Tribes' preferences regarding involvement in the FIP
process. We provided information on our plan to prepare a FIP to ensure
air quality protection while preventing delays in oil and natural gas
production. We solicited the Tribes' input on the FIP development. The
Council members present at the consultation meeting indicated that they
strongly desired this FIP to be consistent with North Dakota's
requirements for oil and natural gas production facilities in order to
keep a level playing field for development and continue uninterrupted
development of a key economic resource for the Tribes. The Council
members expressed interest in the future delegation of this FIP so that
the Tribes can implement the rule in place of us. The Council members
also expressed interest in providing the Tribes' assistance in setting
up a public hearing for the rule.
As noted above, the Three Affiliated Tribes of the Mandan, Hidatsa
and Arikara Nation have indicated preliminary interest in seeking
administrative delegation of the Federal Tribal NSR rule to assist us
with administration of that rule. We will continue to work with the
Three Affiliated Tribes of the Mandan, Hidatsa, and Arikara Nation if
administrative delegation is something the Tribes decide to pursue.
Information containing the consultation process is contained in the
docket for this rule.
For purposes of the final rule, we specifically solicited
additional comments on the proposed action from tribal officials. We
did not receive any comments on the proposed rule from tribal officials
during the public comment period.
G. Executive Order 13045: Protection of Children From Environmental
Health Risks and Safety Risks
The 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 action is not
subject to EO 13045 because the Agency does not believe the
environmental or safety risks addressed by this action present a
disproportionate risk to children. In addition, this rule requires
control and reduction of emissions of VOCs, which
[[Page 17858]]
will have a beneficial effect on children's health by reducing air
pollution.
H. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
This action is not subject to Executive Order 13211 (66 FR 28355,
May 22, 2001), because it is not a significant regulatory action under
Executive Order 12866.
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, 12(d) (15 U.S.C. 272 note)
directs us 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 us to provide
Congress, through OMB, explanations when the Agency decides not to use
available and applicable voluntary consensus standards.
This rulemaking does not involve technical standards. Therefore, we
did not consider the use of any voluntary consensus standards.
J. Executive Order 12898: Federal Actions To Address Environmental
Justice in Minority Populations and Low-Income Populations
Executive Order 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.
We did a demographic analysis of the areas closest to sources
likely to be covered by this rule, and found disproportionately high
concentrations of minority and low income populations. As detailed in
our response to comments, we took substantial steps to ensure that such
populations were given the opportunity for meaningful participation in
the development of the rule. In addition, we conducted an EJ analysis
that determined that this rule will not have disproportionately high
and adverse human health or environmental effects of their programs,
policies, and activities on minority, low-income, and indigenous
populations, because it ensures compliance with the NAAQS, which
provides environmental and public health protection for all affected
populations, including minority, low-income, and indigenous
populations.\34\
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\34\ The TSD includes a more detailed explanation of the EJ
analysis for this FIP. It can be found in the docket for this rule,
Docket ID: EPA-R08-OAR-2012-0479, which can be accessed at: https://www.regulations.gov.
---------------------------------------------------------------------------
K. Congressional Review Act
The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the
Small Business Regulatory Enforcement Fairness Act of 1996, generally
provides that before a rule may take effect, the agency promulgating
the rule must submit a rule report, which includes a copy of the rule,
to each House of the Congress and to the Comptroller General of the
United States. The EPA will submit a report containing this rule and
other required information to the U.S. Senate, the U.S. House of
Representatives and the Comptroller General of the United States prior
to publication of the rule in the Federal Register. A major rule cannot
take effect until 60 days after it is published in the Federal
Register. This action is not a ``major rule'' as defined by 5 U.S.C.
804(2). This rule will be effective 30 days from the date of
publication, i.e., on April 22, 2013.
L. Judicial Review
Under section 307(b)(1) of the Act, petitions for judicial review
of this action must be filed in the United States Court of Appeals for
the appropriate circuit by May 21, 2013. Any such judicial review is
limited to only those objections that are raised with reasonable
specificity in timely comments. Filing a petition for reconsideration
by the Administrator of this final rule does not affect the finality of
this rule for the purposes of judicial review nor does it extend the
time within which a petition for judicial review may be filed and shall
not postpone the effectiveness of such rule or action. Under section
307(b)(2) of the Act, the requirements of this final action may not be
challenged later in civil or criminal proceedings brought by us to
enforce these requirements.
List of Subjects in 40 CFR Part 49
Environmental protection, Administrative practice and procedure,
Air pollution control, Indians, Intergovernmental relations, Reporting
and recordkeeping requirements.
Dated: March 1, 2013.
Bob Perciasepe,
Acting Administrator.
40 CFR part 49 is amended as follows:
PART 49--[AMENDED]
0
1. The authority citation for part 49 continues to read as follows:
Authority: 42 U.S.C. 7401, et seq.
PART 49--INDIAN COUNTRY: AIR QUALITY PLANNING AND MANAGEMENT
Subpart K--Implementation Plans for Tribes--Region VIII
0
2. Add Sec. Sec. 49.4161 through 49.4168 and an undesignated center
heading to appear immediately before the newly added Sec. 49.4161 to
read as follows:
* * * * *
Federal Implementation Plan for Oil and Natural Gas Well Production
Facilities; Fort Berthold Indian Reservation (Mandan, Hidatsa and
Arikara Nation), North Dakota
Sec.
Subpart
49.4161 Introduction.
49.4162 Delegation of authority of administration to the tribes.
49.4163 General provisions.
49.4164 Construction and operational control measures.
49.4165 Control equipment requirements.
49.4166 Monitoring requirements.
49.4167 Recordkeeping requirements.
49.4168 Notification and reporting requirements.
* * * * *
Federal Implementation Plan for Oil and Natural Gas Well Production
Facilities; Fort Berthold Indian Reservation (Mandan, Hidatsa and
Arikara Nation), North Dakota
Sec. 49.4161 Introduction.
(a) What is the purpose of Sec. Sec. 49.4161 through 49.4168?
Sections 49.4161 through 49.4168 establish legally and practicably
enforceable requirements to control and reduce VOC emissions from well
completion operations, well recompletion operations, production
operations, and storage operations at existing, new and modified oil
and natural gas production facilities.
(b) Am I subject to Sec. Sec. 49.4161 through 49.4168? Sections
49.4161 through 49.4168 apply to each owner or operator constructing,
modifying or operating an oil and natural gas production facility
[[Page 17859]]
producing from the Bakken Pool with one or more oil and natural gas
wells, for any one of which completion or recompletion operations are/
were performed on or after August 12, 2007, that is located on the Fort
Berthold Indian Reservation, which is defined by the Act of March 3,
1891 (26 Statute 1032) and which includes all lands added to the
Reservation by Executive Order of June 17, 1892 (the ``Fort Berthold
Indian Reservation''). For the purposes of this subpart, the date that
the first well completion operation at a new oil and natural gas
production facility was initiated is the date that initial construction
has commenced. For the purposes of this subpart, the date that a new
well completion operation or the date that an existing well
recompletion operation at an existing oil and natural gas production
facility is initiated is the date that a modification has commenced.
(c) When must I comply with Sec. Sec. 49.4161 through 49.4168?
Compliance with Sec. Sec. 49.4161 through 49.4168 is required no later
than June 20, 2013 or upon initiation of well completion operations or
well recompletion operations, whichever is later.
Sec. 49.4162 Delegation of authority of administration to the tribes.
(a) What is the purpose of this section? The purpose of this
section is to establish the process by which the Regional Administrator
may delegate to the Mandan, Hidatsa and Arikara Nation the authority to
assist the EPA with administration of this Federal Implementation Plan
(FIP). This section provides for administrative delegation and does not
affect the eligibility criteria under 40 CFR 49.6 for treatment in the
same manner as a state.
(b) How does the Tribe request delegation? In order to be delegated
authority to assist us with administration of this FIP, the authorized
representative of the Mandan, Hidatsa and Arikara Nation must submit a
request to the Regional Administrator that:
(1) Identifies the specific provisions for which delegation is
requested;
(2) Includes a statement by the Mandan, Hidatsa and Arikara
Nation's legal counsel (or equivalent official) that includes the
following information:
(i) A statement that the Mandan, Hidatsa and Arikara Nation are an
Indian Tribe recognized by the Secretary of the Interior;
(ii) A descriptive statement demonstrating that the Mandan, Hidatsa
and Arikara Nation are currently carrying out substantial governmental
duties and powers over a defined area and that meets the requirements
of Sec. 49.7(a)(2); and
(iii) A description of the laws of the Mandan, Hidatsa and Arikara
Nation that provide adequate authority to carry out the aspects of the
rule for which delegation is requested.
(3) Demonstrates that the Mandan, Hidatsa and Arikara Nation have,
or will have, adequate resources to carry out the aspects of the rule
for which delegation is requested.
(c) How is the delegation of administration accomplished? (1) A
Delegation of Authority Agreement will set forth the terms and
conditions of the delegation, will specify the rule and provisions that
the Mandan, Hidatsa and Arikara Nation shall be authorized to implement
on behalf of the EPA, and shall be entered into by the Regional
Administrator and the Mandan, Hidatsa and Arikara Nation. The Agreement
will become effective upon the date that both the Regional
Administrator and the authorized representative of the Mandan, Hidatsa
and Arikara Nation have signed the Agreement. Once the delegation
becomes effective, the Mandan, Hidatsa and Arikara Nation will be
responsible, to the extent specified in the Agreement, for assisting us
with administration of this FIP and shall act as the Regional
Administrator as that term is used in these regulations. Any Delegation
of Authority Agreement will clarify the circumstances in which the term
``Regional Administrator''' found throughout this FIP is to remain the
EPA Regional Administrator and when it is intended to refer to the
``Mandan, Hidatsa and Arikara Nation,'' instead.
(2) A Delegation of Authority Agreement may be modified, amended,
or revoked, in part or in whole, by the Regional Administrator after
consultation with the Mandan, Hidatsa and Arikara Nation.
(d) How will any delegation of authority agreement be publicized?
The Regional Administrator shall publish a notice in the Federal
Register informing the public of any delegation of authority agreement
with the Mandan, Hidatsa and Arikara Nation to assist us with
administration of all or a portion of this FIP and will identify such
delegation in the FIP. The Regional Administrator shall also publish an
announcement of the delegation of authority agreement in local
newspapers.
Sec. 49.4163 General provisions.
(a) Definitions. As used in Sec. Sec. 49.4161 through 49.4168, all
terms not defined herein shall have the meaning given them in the Act,
in subpart A and subpart OOOO of 40 CFR part 60, in the Prevention of
Significant Deterioration regulations at 40 CFR 52.21, or in the
Federal Minor New Source Review Program in Indian Country at 40 CFR
49.151. The following terms shall have the specific meanings given
them.
(1) Bakken Pool means Oil produced from the Bakken, Three Forks,
and Sanish Formations.
(2) Breathing losses means natural gas emissions from fixed roof
tanks resulting from evaporative losses during storage.
(3) Casinghead natural gas means the associated natural gas that
naturally dissolves out of reservoir fluids during well completion
operations and recompletion operations due to the pressure relief that
occurs as the reservoir fluids travel up the well casinghead.
(4) Closed vent system means a system that is not open to the
atmosphere and that is composed of hard-piping, ductwork, connections,
and, if necessary, flow-inducing devices that transport natural gas
from a piece or pieces of equipment to a control device or back to a
process.
(5) Enclosed combustor means a thermal oxidation system with an
enclosed combustion chamber that maintains a limited constant
temperature by controlling fuel and combustion air.
(6) Existing facility means an oil and natural gas production
facility that begins actual construction prior to the effective date of
the ``Federal Implementation Plan for Oil and Natural Gas Well
Production Facilities; Fort Berthold Indian Reservation (Mandan,
Hidatsa and Arikara Nation), North Dakota''.
(7) Flashing losses means natural gas emissions resulting from the
presence of dissolved natural gas in the produced oil and the produced
water, both of which are under high pressure, that occurs as the
produced oil and produced water is transferred to storage tanks or
other vessels that are at atmospheric pressure.
(8) Modified facility means a facility which has undergone the
addition, completion, or recompletion of one or more oil and natural
gas wells, and/or the addition of any associated equipment necessary
for production and storage operations at an existing facility.
(9) New facility means an oil and natural gas production facility
that begins actual construction after the effective date of the
``Federal Implementation Plan for Oil and Natural Gas Well Production
Facilities; Fort Berthold Indian Reservation (Mandan,
[[Page 17860]]
Hidatsa and Arikara Nation), North Dakota''.
(10) Oil means hydrocarbon liquids.
(11) Oil and natural gas production facility means all of the air
pollution emitting units and activities located on or integrally
connected to one or more oil and natural gas wells that are necessary
for production operations and storage operations.
(12) Oil and natural gas well means a single well that extracts
subsurface reservoir fluids containing a mixture of oil, natural gas,
and water.
(13) Owner or operator means any person who owns, leases, operates,
controls, or supervises an oil and natural gas production facility.
(14) Permit to construct or construction permit means a permit
issued by the Regional Administrator pursuant to 40 CFR 49.151, 52.10
or 52.21, or a permit issued by a tribe pursuant to a program approved
by the Administrator under 40 CFR part 51, subpart I, authorizing the
construction or modification of a stationary source.
(15) Permit to operate or operating permit means a permit issued by
the Regional Administrator pursuant to 40 CFR part 71, or by a tribe
pursuant to a program approved by the Administrator under 40 CFR part
51 or 40 CFR part 70, authorizing the operation of a stationary source.
(16) Pit flare means an ignition device, installed horizontally or
vertically and used in oil and natural gas production operations to
combust produced natural gas and natural gas emissions.
(17) Produced natural gas means natural gas that is separated from
extracted reservoir fluids during production operations.
(18) Produced oil means oil that is separated from extracted
reservoir fluids during production operations.
(19) Produced oil storage tank means a unit that is constructed
primarily of non-earthen materials (such as steel, fiberglass, or
plastic) which provides structural support and is designed to contain
an accumulation of produced oil.
(20) Produced water means water that is separated from extracted
reservoir fluids during production operations.
(21) Produced water storage tank means a unit that is constructed
primarily of non-earthen materials (such as steel, fiberglass, or
plastic) which provides structural support and is designed to contain
an accumulation of produced water.
(22) Production operations means the extraction and separation of
reservoir fluids from an oil and natural gas well, using separators and
heater-treater systems. A separator is a pressurized vessel designed to
separate reservoir fluids into their constituent components of oil,
natural gas and water. A heater-treater is a unit that heats the
reservoir fluid to break oil/water emulsions and to reduce the oil
viscosity. The water is then typically removed by using gravity to
allow the water to separate from the oil.
(23) Regional Administrator means the Regional Administrator of EPA
Region 8 or an authorized representative of the Regional Administrator.
(24) Standing losses means natural gas emissions from fixed roof
tanks as a result of evaporative losses during storage.
(25) Storage operations means the transfer of produced oil and
produced water to storage tanks, the filling of the storage tanks, the
storage of the produced oil and produced water in the storage tanks,
and the draining of the produced oil and produced water from the
storage tanks.
(26) Supervisory Control and Data Acquisition (SCADA) system
generally refers to industrial control computer systems that monitor
and control industrial infrastructure or facility-based processes.
(27) Utility flare means thermal oxidation system using an open
(without enclosure) flame. An enclosed combustor as defined in
Sec. Sec. 49.4161 through 49.4168 is not considered a flare.
(28) Visible Smoke emissions means a pollutant generated by thermal
oxidation in a flare or enclosed combustor and occurring immediately
downstream of the flame. Visible smoke occurring within, but not
downstream of, the flame, is not considered to constitute visible smoke
emissions.
(29) Well completion means the process that allows for the flowback
of oil and natural gas from newly drilled wells to expel drilling and
reservoir fluids and tests the reservoir flow characteristics, which
may vent produced hydrocarbons to the atmosphere via an open pit or
tank.
(30) Well completion operation means any oil and natural gas well
completion using hydraulic fracturing occurring at an oil and natural
gas production facility.
(31) Well recompletion operation means any oil and natural gas well
completion using hydraulic refracturing occurring at an oil and natural
gas production facility.
(32) Working losses means natural gas emissions from fixed roof
tanks resulting from evaporative losses during filling and emptying
operations.
(b) Requirement for testing. The Regional Administrator may require
that an owner or operator of an oil and natural gas production facility
demonstrate compliance with the requirements of the ``Federal
Implementation Plan for Oil and Natural Gas Well Production Facilities;
Fort Berthold Indian Reservation (Mandan, Hidatsa and Arikara Nation),
North Dakota'' by performing a source test and submitting the test
results to the Regional Administrator. Nothing in the ``Federal
Implementation Plan for Oil and Natural Gas Well Production Facilities;
Fort Berthold Indian Reservation (Mandan, Hidatsa and Arikara Nation),
North Dakota'' limits the authority of the Regional Administrator to
require, in an information request pursuant to section 114 of the Act,
an owner or operator of an oil and natural gas production facility
subject to the ``Federal Implementation Plan for Oil and Natural Gas
Production Facilities, Fort Berthold Indian Reservation (Mandan,
Hidatsa and Arikara Nation)'' to demonstrate compliance by performing
testing, even where the facility does not have a permit to construct or
a permit to operate.
(c) Requirement for monitoring, recordkeeping, and reporting.
Nothing in ``Federal Implementation Plan for Oil and Natural Gas
Production Facilities, Fort Berthold Indian Reservation (Mandan,
Hidatsa and Arikara Nation)'' precludes the Regional Administrator from
requiring monitoring, recordkeeping and reporting, including
monitoring, recordkeeping and reporting in addition to that already
required by an applicable requirement in these rules, in a permit to
construct or permit to operate in order to ensure compliance.
(d) Credible evidence. For the purposes of submitting reports or
establishing whether or not an owner or operator of an oil and natural
gas production facility has violated or is in violation of any
requirement, nothing in the ``Federal Implementation Plan for Oil and
Natural Gas Well Production Facilities; Fort Berthold Indian
Reservation (Mandan, Hidatsa and Arikara Nation), North Dakota'' shall
preclude the use, including the exclusive use, of any credible evidence
or information, relevant to whether a facility would have been in
compliance with applicable requirements if the appropriate performance
or compliance test had been performed.
[[Page 17861]]
Sec. 49.4164 Construction and operational control measures.
(a) Each owner or operator must operate and maintain all liquid and
gas collection, storage, processing and handling operations, regardless
of size, so as to minimize leakage of natural gas emissions to the
atmosphere.
(b) During all oil and natural gas well completion operations or
recompletion operations at an oil and natural gas production facility
and prior to the first date of production of each oil and natural gas
well, each owner or operator must, at a minimum, route all casinghead
natural gas to a utility flare or a pit flare capable of reducing the
mass content of VOC in the natural gas emissions vented to it by at
least 90.0 percent or greater and operated as specified in Sec. Sec.
49.4165 and 49.4166.
(c) Beginning with the first date of production from any one oil
and natural gas well at an oil and natural gas production facility,
each owner or operator must, at a minimum, route all natural gas
emissions from production operations and storage operations to a
control device capable of reducing the mass content of VOC in the
natural gas emissions vented to it by at least 90.0 percent or greater
and operated as specified in Sec. Sec. 49.4165 and 49.4166.
(d) Within ninety (90) days of the first date of production from
any oil and natural gas well at an oil and natural gas production
facility, each owner or operator must:
(1) Route the produced natural gas from the production operations
through a closed-vent system to:
(i) An operating system designed to recover and inject all the
produced natural gas into a natural gas gathering pipeline system for
sale or other beneficial purpose; or
(ii) A utility flare or equivalent combustion device capable of
reducing the mass content of VOC in the produced natural gas vented to
the device by at least 98.0 percent or greater and operated as
specified in Sec. Sec. 49.4165 and 49.4166.
(2) Route all standing, working, breathing, and flashing losses
from the produced oil storage tanks and any produced water storage tank
interconnected with the produced oil storage tanks through a closed-
vent system to:
(i) An operating system designed to recover and inject the natural
gas emissions into a natural gas gathering pipeline system for sale or
other beneficial purpose; or
(ii) An enclosed combustor or utility flare capable of reducing the
mass content of VOC in the natural gas emissions vented to the device
by at least 98.0 percent or greater and operated as specified in
Sec. Sec. 49.4165(c) and 49.4166.
(iii) If the uncontrolled potential to emit VOCs from the aggregate
of all produced oil storage tanks and produced water storage tanks
interconnected with produced oil storage tanks at an oil and natural
gas production facility is less than, and reasonably expected to remain
below, 20 tons in any consecutive 12-month period, then, upon prior
written approval by the EPA the owner or operator may use a pit flare,
an enclosed combustor or a utility flare that is capable of reducing
the mass content of VOC in the natural gas emissions from the storage
tanks vented to the device by only 90.0 percent.
(e) In the event that pipeline injection of all or part of the
natural gas collected in an operating system designed to recover and
inject natural gas becomes temporarily infeasible and there is no
operational enclosed combustor or utility flare at the facility, the
owner or operator must route the natural gas that cannot be injected
through a closed-vent system to a pit flare operated as specified in
Sec. Sec. 49.4165 and 49.4166.
(f) Produced oil storage tanks and any produced water storage tanks
interconnected with produced oil storage tanks subject to the
requirements specified in 40 CFR part 60, subpart OOOO are considered
to meet the requirements of Sec. 49.4164(d)(2). No further
requirements apply for such storage tanks under Sec. 49.4164(d)(2).
Sec. 49.4165 Control equipment requirements.
(a) Covers. Each owner or operator must equip all openings on each
produced oil storage tank and produced water storage tank
interconnected with produced oil storage tanks with a cover to ensure
that all natural gas emissions are efficiently being routed through a
closed-vent system to a vapor recovery system, an enclosed combustor, a
utility flare, or a pit flare.
(1) Each cover and all openings on the cover (e.g., access hatches,
sampling ports, pressure relief valves (PRV), and gauge wells) shall
form a continuous impermeable barrier over the entire surface area of
the produced oil and produced water in the storage tank.
(2) Each cover opening shall be secured in a closed, sealed
position (e.g., covered by a gasketed lid or cap) whenever material is
in the unit on which the cover is installed except during those times
when it is necessary to use an opening as follows:
(i) To add material to, or remove material from the unit (this
includes openings necessary to equalize or balance the internal
pressure of the unit following changes in the level of the material in
the unit);
(ii) To inspect or sample the material in the unit; or
(iii) To inspect, maintain, repair, or replace equipment located
inside the unit.
(3) Each thief hatch cover shall be weighted and properly seated.
(4) Each PRV shall be set to release at a pressure that will ensure
that natural gas emissions are routed through the closed-vent system to
the vapor recovery system, the enclosed combustor, or the utility flare
under normal operating conditions.
(b) Closed-vent systems. Each owner or operator must meet the
following requirements for closed-vent systems:
(1) Each closed-vent system must route all produced natural gas and
natural gas emissions from production and storage operations to the
natural gas sales pipeline or the control devices required by paragraph
(a) of this section.
(2) All vent lines, connections, fittings, valves, relief valves,
or any other appurtenance employed to contain and collect natural gas,
vapor, and fumes and transport them to a natural gas sales pipeline and
any VOC control equipment must be maintained and operated properly at
all times.
(3) Each closed-vent system must be designed to operate with no
detectable natural gas emissions.
(4) If any closed-vent system contains one or more bypass devices,
except as provided for in paragraph (b)(4)(iii) of this section, that
could be used to divert all or a portion of the natural gas emissions,
from entering a natural gas sales pipeline and/or any control devices,
the owner or operator must meet the one of following requirements for
each bypass device:
(i) At the inlet to the bypass device that could divert the natural
gas emissions away from a natural gas sales pipeline or a control
device and into the atmosphere, properly install, calibrate, maintain,
and operate a natural gas flow indicator that is capable of taking
continuous readings and sounding an alarm when the bypass device is
open such that natural gas emissions are being, or could be, diverted
away from a natural gas sales pipeline or a control device and into the
atmosphere;
(ii) Secure the bypass device valve installed at the inlet to the
bypass device in the non-diverting position using a car-seal or a lock-
and-key type configuration;
(iii) Low leg drains, high point bleeds, analyzer vents, open-ended
valves or lines, and safety devices are not subject
[[Page 17862]]
to the requirements applicable to bypass devices.
(c) Enclosed combustors and utility flares. Each owner or operator
must meet the following requirements for enclosed combustors and
utility flares:
(1) For each enclosed combustor or utility flare, the owner or
operator must follow the manufacturer's written operating instructions,
procedures and maintenance schedule to ensure good air pollution
control practices for minimizing emissions;
(2) For each enclosed combustor or utility flare, the owner or
operator must ensure there is sufficient capacity to reduce the mass
content of VOC in the produced natural gas and natural gas emissions
routed to it by at least 98.0 percent for the minimum and maximum
natural gas volumetric flow rate and BTU content routed to the device;
(3) Each enclosed combustor or utility flare must be operated to
reduce the mass content of VOC in the produced natural gas and natural
gas emissions routed to it by at least 98.0 percent;
(4) The owner or operator must ensure that each utility flare is
designed and operated in accordance with the requirements of 40 CFR
60.18(b) for such flares, except for Sec. 60.18(c)(2) and (f)(2) for
those utility flares operated with an electronically controlled
automatic igniter.
(5) The owner or operator must ensure that each enclosed combustor
is:
(i) A model demonstrated by a manufacturer to the meet the VOC
destruction efficiency requirements of Sec. Sec. 49.4161 through
49.4168 using the procedure specified in 40 CFR part 60, subpart OOOO
at Sec. 60.5413(d) by the due date of the first annual report as
specified in Sec. 49.4168(b); or
(ii) Demonstrated to meet the VOC destruction efficiency
requirements of Sec. Sec. 49.4161 through 49.4168 using EPA approved
performance test methods specified in 40 CFR part 60, subpart OOOO at
Sec. 60.5413(b) by the due date of the first annual report as
specified in Sec. 49.4168(b).
(6) The owner or operator must ensure that each enclosed combustor
and utility flare is:
(i) Operated properly at all times that produced natural gas and/or
natural gas emissions are routed to it;
(ii) Operated with a liquid knock-out system to collect any
condensable vapors (to prevent liquids from going through the control
device);
(iii) Equipped with a flash-back flame arrestor;
(iv) Equipped with one of the following:
(A) A continuous burning pilot flame.
(B) An electronically controlled automatic igniter;
(v) Equipped with a monitoring system for continuous recording of
the parameters that indicate proper operation of each enclosed
combustor, utility flare, continuous burning pilot flame, and
electronically controlled automatic igniter, such as a chart recorder,
data logger or similar devices;
(vi) Maintained in a leak-free condition; and
(vii) Operated with no visible smoke emissions.
(d) Pit Flares. Each owner or operator must meet the following
requirements for pit flares:
(1) The owner or operator must develop written operating
instructions, operating procedures and maintenance schedules to ensure
good air pollution control practices for minimizing emissions from the
pit flare based on the site-specific design.
(2) The owner or operator must only use a pit flare for the
following operations:
(i) To control produced natural gas and natural gas emissions
during well completion operations or recompletion operations;
(ii) To control produced natural gas and natural gas emissions in
the event that natural gas recovered for pipeline injection must be
diverted to a backup control device because injection is temporarily
infeasible and there is no operational enclosed combustor or utility
flare at the oil and natural gas production facility. Use of the pit
flare for this situation is limited to a maximum of 500 hours in any
twelve (12) consecutive months; or
(iii) Control of standing, working, breathing, and flashing losses
from the produced oil storage tanks and any produced water storage tank
interconnected with the produced oil storage tanks if the uncontrolled
potential VOC emissions from the aggregate of all produced oil storage
tanks and produced water storage tanks interconnected with produced oil
storage tanks is less than, and reasonably expected to remain below, 20
tons in any consecutive 12-month period.
(3) The owner or operator must only use the pit flare under the
following conditions and limitations:
(i) The pit flare is operated to reduce the mass content of VOC in
the produced natural gas and natural gas emissions routed to it by at
least 90.0 percent;
(ii) The pit flare is operated in accordance with the site-specific
written operating instructions, operating procedures, and maintenance
schedules to ensure good air pollution control practices for minimizing
emissions;
(iii) The pit flare is operated with no visible smoke emissions;
(iv) The pit flare is equipped with an electronically controlled
automatic igniter;
(v) The pit flare is visually inspected for the presence of a flame
anytime produced natural gas or natural gas emissions are being routed
to it. Should the flame fail, the flame must be relit as soon as safely
possible and the electronically controlled automatic igniter must be
repaired or replaced before the pit flare is utilized again; and
(vi) The owner or operator does not deposit or cause to be
deposited into a flare pit any oil field fluids or oil and natural gas
wastes other than those designed to go to the pit flare.
(e) Other Control Devices. Upon prior written approval by the EPA,
the owner or operator may use control devices other than those listed
above that are determined by EPA to be capable of reducing the mass
content of VOC in the natural gas routed to it by at least 98.0
percent, provided that:
(1) In operating such control devices, the owner or operator must
follow the manufacturer's written operating instructions, procedures
and maintenance schedule to ensure good air pollution control practices
for minimizing emissions; and
(2) The owner or operator must ensure there is sufficient capacity
to reduce the mass content of VOC in the produced natural gas and
natural gas emissions routed to such other control devices by at least
98.0 percent for the minimum and maximum natural gas volumetric flow
rate and BTU content routed to each device.
(3) The owner or operator must operate such a control device to
reduce the mass content of VOC in the produced natural gas and natural
gas emissions routed to it by at least 98.0 percent.
Sec. 49.4166 Monitoring requirements.
(a) Each owner and operator must measure the barrels of oil
produced at the oil and natural gas production facility each time the
oil is unloaded from the produced oil storage tanks using the
methodologies of tank gauging or positive displacement metering system,
as appropriate, as established by the U.S. Department of the Interior's
Bureau of Land Management at 43 CFR part 3160, in the ``Onshore Oil and
Gas Operations; Federal and Indian Oil & Gas Leases; Onshore Oil and
Gas Order No. 4; Measurement of Oil''.
(b) Each owner or operator must monitor the hours that each pit
flare is
[[Page 17863]]
operated to control produced natural gas and natural gas emissions in
the event that natural gas recovered for pipeline injection must be
diverted to a backup control device because injection is temporarily
infeasible and there is no enclosed combustor or utility flare at the
oil and natural gas production facility.
(c) Each owner or operator must monitor the volume of produced
natural gas sent to each enclosed combustor, utility flare, and pit
flare at all times. Methods to measure the volume include, but are not
limited to, direct measurement and gas-to-oil ratio (GOR) laboratory
analyses.
(d) Each owner or operator must monitor the volume of standing,
working, breathing, and flashing losses from the produced oil and
produced water storage tanks sent to each vapor recovery system,
enclosed combustor, utility flare, and pit flare at all times. Methods
to measure the volume include, but are not limited to, direct
measurement or GOR laboratory analyses.
(e) Each owner or operator must perform quarterly visual
inspections of tank thief hatches, covers, seals, PRVs, and closed vent
systems to ensure proper condition and functioning and repair any
damaged equipment. The quarterly inspections must be performed while
the produced oil and produced water storage tanks are being filled.
(f) Each owner or operator must perform quarterly visual
inspections of the peak pressure and vacuum values in each closed vent
system and control system for the produced oil and produced water
storage tanks to ensure that the pressure and vacuum relief set-points
are not being exceeded in a way that has resulted, or may result, in
venting and possible damage to equipment. The quarterly inspections
must be performed while the produced oil and produced water storage
tanks are being filled.
(g) Each owner or operator must monitor the operation of each
enclosed combustor, utility flare, and pit flare to confirm proper
operation as follows:
(1) Continuously monitor all variable operational parameters
specified in the written operating instructions and procedures,
including continuous burning pilot flame, electronically controlled
automatic igniters, and monitoring system failures, using a malfunction
alarm and remote notification system, where such systems are available,
or continuously monitor under an equivalent alternative protocol upon
prior written approval by the EPA;
(2) Perform a physical inspection of all equipment associated with
each enclosed combustor, utility flare, and pit flare each time an
operator is on site, at a minimum quarterly, to ensure system
integrity;
(3) Monitor for visible smoke during operation of any enclosed
combustor, utility flare or pit flare each time an operator is on site,
at a minimum quarterly. Upon observation of visible smoke, use EPA
Reference Method 22 of 40 CFR part 60, Appendix A, to determine whether
visible smoke emissions are present. The observation period shall be 2
hours. Visible smoke emissions are present if smoke is observed for
more than 5 minutes in any 2 consecutive hours; and
(4) Respond to any observation of any continuous burning pilot
flame failure, electronically controlled automatic igniter failure, or
improper monitoring equipment operation and ensure the equipment is
returned to proper operation as soon as practicable and safely possible
after an observation or an alarm sounds.
(h) Where sufficient to meet the monitoring and recordkeeping
requirements in Sec. Sec. 49.4166 and 49.4167, the owner or operator
may use a Supervisory Control and Data Acquisition (SCADA) system to
monitor and record the required data in Sec. Sec. 49.4161 through
49.4168.
(i) Other Monitoring Options. The owner or operator may use
equivalent methods of monitoring other than those listed above upon
prior written approval by the EPA.
Sec. 49.4167 Recordkeeping requirements.
(a) Each owner or operator must maintain the following records:
(1) The measured barrels of oil produced at the oil and natural gas
production facility each time the oil is unloaded from the produced oil
storage tanks;
(2) The volume of produced natural gas sent to each enclosed
combustor, utility flare, and pit flare at all times;
(3) The volume of natural gas emissions from the produced oil
storage tanks and produced water storage tanks sent to each enclosed
combustor, utility flare, and pit flare at all times;
(4) A summary of each oil and natural gas well completion operation
and recompletion operation at an oil and natural gas production
facility. Each summary shall include:
(i) The latitude and longitude location of the oil and natural gas
well in decimal format;
(ii) The date, time, and duration in hours of flowback from the oil
and natural gas well;
(iii) The date, time, and duration in hours of any venting of
casinghead natural gas from the oil and natural gas well; and
(iv) Specific reasons for each instance of venting in lieu of
capture or combustion.
(5) For each enclosed combustor, utility flare, and pit flare at an
oil and natural gas production facility:
(i) Written, site-specific designs, operating instructions,
operating procedures and maintenance schedules;
(ii) Records of all required monitoring of operations;
(iii) Records of any deviations from the operating parameters
specified by the written site-specific designs, operating instructions,
and operating procedures. The records must include the enclosed
combustor, utility flare, or pit flare's total operating time during
which a deviation occurred, the date, time and length of time that
deviations occurred, and the corrective actions taken and any
preventative measures adopted to operate the device within that
operating parameter;
(iv) Records of any instances in which the pilot flame is not
present, electronically controlled automatic igniter is not
functioning, or the monitoring equipment is not functioning in the
enclosed combustor, the utility flare, or the pit flare, the date and
times of the occurrence, the corrective actions taken, and any
preventative measures adopted to prevent recurrence of the occurrence;
(v) Records of any instances in which a recording device installed
to record data from the enclosed combustor, utility flare, or pit flare
is not operational; and
(vi) Records of any time periods in which visible smoke emissions
are observed emanating from the enclosed combustor, utility flare, or
pit flare.
(6) For each pit flare at an oil and natural gas production
facility, a demonstration of compliance with the use restrictions set
forth in Sec. 49.4165(d)(2)(ii) is made by keeping records in a log
book, or similar recording system, during each period of time that the
pit flare is operating. The records must contain the following
information:
(i) Date and time the pit flare was started up and subsequently
shut down;
(ii) Total hours operated when pipeline injection was temporarily
infeasible for the current calendar month plus the previous consecutive
eleven (11) calendar months; and
(iii) Brief descriptions of the justification for each period of
operation.
(7) Records of any instances in which any closed-vent system or
control device was bypassed or down, the
[[Page 17864]]
reason for each incident, its duration, the volume of natural gas
emissions released, and the corrective actions taken and any
preventative measures adopted to avoid such bypasses or downtimes; and
(8) Documentation of all produced oil storage tank and produced
water storage tank inspections required in Sec. 49.4166(e) and (f).
All inspection records must include, at a minimum, the following
information:
(i) The date of the inspection;
(ii) The findings of the inspection;
(iii) Any adjustments or repairs made as a result of the
inspections, and the date of the adjustment or repair; and
(iv) The inspector's name and signature.
(b) Each owner or operator must keep all records required by this
section onsite at the facility or at the location that has day-to-day
operational control over the facility and must make the records
available to the EPA upon request.
(c) Each owner or operator must retain all records required by this
section for a period of at least five (5) years from the date the
record was created.
Sec. 49.4168 Notification and reporting requirements.
(a) Each owner or operator must submit any documents required under
this section to: U.S. Environmental Protection Agency, Region 8 Office
of Enforcement, Compliance & Environmental Justice, Air Toxics and
Technical Enforcement Program, 8ENF-AT, 1595 Wynkoop Street, Denver,
Colorado 80202. Documents may be submitted electronically to
r8airreportenforcement@epa.gov.
(b) Each owner and operator must submit an annual report containing
the information specified in paragraphs (b)(1) through (4) of this
section. Each annual report is due August 15th every year and must
cover all information for the previous calendar year. The initial
report must cover the cumulative information for that year. If you own
or operate more than one oil and natural gas production facility, you
may submit one report for multiple oil and natural gas production
facilities provided the report contains all of the information required
as specified in paragraphs (b)(1) through (4) of this section. Annual
reports may coincide with title V reports as long as all the required
elements of the annual report are included. The EPA may approve a
common schedule on which reports required by Sec. Sec. 49.4161 through
49.4168 may be submitted as long as the schedule does not extend the
reporting period.
(1) The company name and the address of the oil and natural gas
production facility or facilities.
(2) An identification of each oil and natural gas production
facility being included in the annual report.
(3) The beginning and ending dates of the reporting period.
(4) For each oil and natural gas production facility, the
information in paragraphs (b)(4)(i) through (iv) of this section.
(i) A summary of all required records identifying each oil and
natural gas well completion or recompletion operation for each oil and
natural gas production facility conducted during the reporting period;
(ii) An identification of the first date of production for each oil
and natural gas well at each oil and natural gas production facility
that commenced production during the reporting period; and
(iii) A summary of cases where construction or operation was not
performed in compliance with the requirements specified in Sec.
49.4164, Sec. 49.4165, or Sec. 49.4166 for each oil and natural gas
well at each oil and natural gas production facility, and the
corrective measures taken.
(iv) A certification by a responsible official of truth, accuracy
and completeness. This certification shall state that, based on
information and belief formed after reasonable inquiry, the statements
and information in the document are true, accurate and complete.
[FR Doc. 2013-05666 Filed 3-21-13; 8:45 am]
BILLING CODE 6560-50-P