Air Plan Approval; Maryland; Negative Declaration for the Oil and Gas Industry, 52993-52996 [2021-20494]
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Federal Register / Vol. 86, No. 183 / Friday, September 24, 2021 / Rules and Regulations
review may be filed, and shall not
postpone the effectiveness of such rule
or action. This action may not be
challenged later in proceedings to
enforce its requirements. (See section
307(b)(2).)
List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Best available retrofit
technology, Carbon monoxide,
Incorporation by reference,
Intergovernmental relations, Lead,
Nitrogen dioxide, Ozone, Particulate
matter, Reporting and recordkeeping
requirements, Regional haze, Sulfur
dioxide, Visibility, Volatile organic
compounds.
Dated: September 17, 2021.
David Gray,
Acting Regional Administrator, Region 6.
For the reasons stated in the
preamble, the Environmental Protection
Agency amends 40 CFR part 52 as
follows:
PART 52—APPROVAL AND
PROMULGATION OF
IMPLEMENTATION PLANS
Authority: 42 U.S.C. 7401 et seq.
Subpart T—Louisiana
2. In § 52.970(e), the second table
titled ‘‘EPA Approved Louisiana
Nonregulatory Provisions and QuasiRegulatory Measures’’ is amended by
adding the entry ‘‘Louisiana Regional
Haze Progress Report’’ at the end of the
table to read as follows:
■
§ 52.970
*
1. The authority citation for part 52
continues to read as follows:
■
52993
Identification of plan.
*
*
(e) * * *
*
*
EPA APPROVED LOUISIANA NONREGULATORY PROVISIONS AND QUASI-REGULATORY MEASURES
Name of SIP
provision
State
submittal
date/
effective
date
Applicable geographic or
nonattainment area
*
Louisiana Regional
Haze Progress
Report.
*
Statewide ........................................
[FR Doc. 2021–20617 Filed 9–23–21; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R03–OAR–2020–0528; FRL–8974–02–
R3]
Air Plan Approval; Maryland; Negative
Declaration for the Oil and Gas
Industry
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
The Environmental Protection
Agency (EPA) is approving a state
implementation plan (SIP) revision
submitted by the State of Maryland.
This revision provides Maryland’s
determination, via a negative
declaration, that there are no sources
within its borders subject to EPA’s 2016
Oil and Natural Gas control techniques
guidelines (2016 Oil and Gas CTG). EPA
is approving these revisions to the
Maryland SIP in accordance with the
requirements of the Clean Air Act
(CAA).
SUMMARY:
*
3/25/2021
EPA approval date
*
*
9/24/2021, [Insert Federal Register citation].
the https://www.regulations.gov
website. Although listed in the index,
some information is not publicly
available, e.g., confidential business
information (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 through https://
www.regulations.gov, or please contact
the person identified in the FOR FURTHER
INFORMATION CONTACT section for
additional availability information.
FOR FURTHER INFORMATION CONTACT:
David Talley, Planning &
Implementation Branch (3AD30), Air &
Radiation Division, U.S. Environmental
Protection Agency, Region III, 1650
Arch Street, Philadelphia, Pennsylvania
19103. The telephone number is (215)
814–2117. Mr. Talley can also be
reached via electronic mail at
talley.david@epa.gov.
SUPPLEMENTARY INFORMATION:
I. Background
On February 9, 2021 (86 FR 8742),
EPA published a notice of proposed
rulemaking (NPRM) for the State of
Maryland. In the NPRM, EPA proposed
DATES: This final rule is effective on
approval of Maryland’s negative
October 25, 2021.
declaration SIP submittal for the 2016
Oil and Gas CTG. On June 18, 2020, the
ADDRESSES: EPA has established a
Maryland Department of the
docket for this action under Docket ID
Number EPA–R03–OAR–2020–0528. All Environment (MDE) submitted the
negative declaration for the 2016 Oil
documents in the docket are listed on
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Explanation
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*
*
and Gas CTG as a revision to the
Maryland SIP.
The CAA regulates emissions of
nitrogen oxides (NOX) and volatile
organic compounds (VOCs) to prevent
photochemical reactions that result in
ozone formation. Reasonably available
control technology (RACT) is a strategy
for reducing NOX and VOC emissions
from stationary sources within
designated nonattainment areas
classified as moderate or above that are
not meeting the national ambient air
quality standards (NAAQS) for ozone.
EPA has consistently defined ‘‘RACT’’
as the lowest emission limit that a
particular source is capable of meeting
by the application of the control
technology that is reasonably available
considering technological and economic
feasibility.
Control techniques guidelines (CTGs)
and alternative control techniques
(ACTs) form important components of
the guidance that EPA provides to states
for making RACT determinations. CTGs
are used to presumptively define VOC
RACT for applicable source categories.
CAA section 182(b)(2)(A) requires that
for ozone nonattainment areas classified
as moderate or above, states must revise
their SIPs to include provisions to
implement RACT for each category of
VOC sources covered by a CTG
document. CAA section 184(b)(1)(B)
extends the RACT obligation to all areas
of states within the ozone transport
region (OTR), including Maryland.
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States subject to RACT requirements
are required to enact controls for
sources subject to CTGs that are at least
as stringent as those found within the
CTG, either via the adoption of
regulations or by issuance of single
source permits that outline what the
source is required to do to meet RACT.
On March 6, 2016 (80 FR 12264), EPA
issued a final rule entitled
‘‘Implementation of the 2008 National
Ambient Air Quality Standards for
Ozone: State Implementation Plan
Requirements’’ (2008 Ozone
Implementation Rule). In the preamble
to the final rule, EPA makes clear that
if there are no sources covered by a
specific CTG source category located in
an ozone nonattainment area or an area
in the OTR, the state may submit a
negative declaration for that CTG. See
80 FR 12264, 12278. The same negative
declaration is allowed by the 2015
ozone NAAQS implementation rule.1
On October 27, 2016 (81 FR 74798),
EPA published in the Federal Register
the ‘‘Release of Final Control
Techniques Guidelines for the Oil and
Natural Gas Industry,’’ (2016 Oil and
Gas CTG). This CTG provided
information to state, local, and tribal air
agencies to assist in determining RACT
for VOC emissions from certain VOC
emission sources within the oil and
natural gas industry. The 2016 Oil and
Gas CTG replaces an earlier 1983 CTG
entitled ‘‘Control of Volatile Organic
Compound Equipment Leaks from
Natural Gas/Gasoline Processing Plants.
December 1983.’’ EPA–450/3–83–007
(1983 CTG) 49 FR 4432; February 6,
1984. See 2016 Oil and Gas CTG, p. 8–
1.
II. Summary of SIP Revision and EPA
Analysis
According to Maryland’s June 18,
2020 submittal, MDE conducted a
review of potential sources subject to
the 2016 Oil and Gas CTG. This review
consisted of a search of Maryland’s oil
and gas well records, air permit records,
EPA greenhouse gas reporting records,
and the Standard Industrial
Classification (SIC) system. MDE’s
search identified a total of 13 facilities
in Maryland operating in the
production, processing, or transmission
and storage segments of the oil and
natural gas industry. However, none of
1 The majority of the provisions for implementing
the 2008 ozone NAAQS (including those related to
negative declarations) were retained without
revision for purposes of implementing the 2015
ozone NAAQS. See ‘‘Implementation of the 2015
National Ambient Air Quality Standards for Ozone:
Nonattainment Area State Implementation Plan
Requirements’’ (2015 Ozone Implementation Rule)
83 FR 62998 (December 6, 2018); and 40 CFR
51.1301.
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these facilities had storage tanks or
production wells that met or exceeded
the applicability criteria of the CTG.
MDE identified five facilities in the
natural gas transmission sector, but
determined that none of them had
storage tanks with the potential to emit
(PTE) more than 6 tons per year (tpy) of
VOCs, which is the threshold for
applicability of the CTG.2 Additionally,
MDE identified eight active individual
production wells, but determined that
none of these exceeded the 15 barrel
equivalents per day per well, which is
the threshold for CTG applicability.3
Other specific requirements of the 2016
Oil and Gas CTG and the rationale for
EPA’s proposed action are explained in
the NPRM and will not be restated here.
III. EPA’s Response to Comments
Received
EPA received four sets of comments
on our proposed approval of Maryland’s
June 18, 2020 negative declaration SIP
submittal. One comment was generally
in favor of EPA’s proposed action and
will not be addressed in this action. A
summary of the other comments and
EPA’s response is provided herein. All
comments received are included in the
docket for this action.
Comment 1: The commenter asserts
that the tanks and production wells
identified by MDE as being potentially
subject to the CTG, but determined by
MDE to not meet the applicability
thresholds and therefore not subject to
the 2016 Oil and Gas CTG, should have
mechanisms to limit their PTE to ensure
that they remain below the thresholds.
The commenter provides the example of
synthetic minor permits. The
commenter further asserts that relying
on emission factors or other engineering
estimates would be arbitrary given the
‘‘many variables involved.’’
Response 1: EPA disagrees with the
commenter’s assertions. First, AP42
emissions factors and the engineering
estimates (i.e. modelling) relied upon in
Maryland’s submittal are generally
accepted and are used regularly in place
of direct emissions measurement.
Therefore, MDE’s reliance upon them
for the purposes of this negative
declaration is not ‘‘arbitrary.’’ EPA
further disagrees with the commenter’s
assertion that the reported facilities
should have synthetic minor permits or
other enforceable limits on their PTE,
and that it is ‘‘implausible’’ to claim that
these facilities could have PTEs below
the applicability thresholds absent such
limits. In support of this claim, the
commenter offers merely the ‘‘many
2 See
3 See
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Id. at 3–7.
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variables involved,’’ such as varying
composition of the gas over time. EPA’s
review of Maryland’s submittal shows
that the referenced sources all report
emissions well below the thresholds.
For the potentially affected storage
vessels (tanks), Maryland provided
extensive documentation, including
calculations that considered ambient
temperature variations, throughput, and
chemical composition of the liquids
stored in the tanks. All emissions
reported were considerably under the
applicability threshold for storage
vessels. For example, of the six
potentially affected tanks identified at
the Dominion Cove Point facility, the
highest emissions reported were 0.02
tpy of VOC, which is significantly below
the 6 tpy threshold. See Attachment A
of MDE’s June 18, 2020 submittal. The
overwhelming majority of the tanks
analyzed reported emissions of only a
fraction of a ton per year. The highest
reported emissions were for the two
condensate storage tanks at the Accident
compressor station. Each of those had
calculated emissions of 1.2 tpy, still
well below the threshold. See
Attachment B of MDE’s June 18, 2020
submittal.
Similarly, EPA disagrees that the
identified production wells need
enforceable limits on their production.
First, the commenter has provided no
evidence to contradict MDE’s evaluation
of the wells’ outputs. Second, MDE
certified in their submittal that their
evaluation of the production wells was
based on a search of their permit
records. Each of the listed wells was
constructed under a permit issued by
Maryland. MDE is therefore well
positioned to review the data associated
with each of those permits and make an
accurate determination of each well’s
output. EPA finds no reason to
determine that MDE’s determination
with respect to the wells was
unreasonable.
EPA believes that there is a sufficient
margin between the reported emissions
and the applicability threshold to
determine that the identified sources do
not need enforceable PTE limits in order
for EPA to approve Maryland’s negative
declaration. Furthermore, Federal
regulations are only necessary if a
covered source exceeds the applicability
thresholds established by the CTG.
Maryland has certified that none of the
sources within its jurisdiction exceed
these thresholds. Should any of the
reported sources exceed the thresholds
in the future; or should a new source of
the type covered by the existing CTG
emitting more than either threshold be
constructed in the state after approval of
a negative declaration, EPA expects the
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state to develop a regulation and submit
it to EPA for approval into the SIP in
accordance with the relevant timing
provided for by the CAA. Additionally,
it is likely that any significant change in
the operation of the existing facilities
which would impact their PTE would
be subject to preconstruction review by
MDE. The same is true for the
construction of new sources. At this
time, because Maryland does not have
any sources subject to the 2016 Oil and
Gas CTG, no regulation is required to be
developed and submitted for EPA
approval. Therefore, we disagree with
the commenter and are finalizing our
approval of Maryland’s negative
declaration.
Comment 2: The commenter asserts
that EPA should disapprove MDE’s June
18, 2020 submittal because it relies on
TANKS modelling, which utilizes
outdated information, including
temperature/climate data which is ‘‘all
over 10 years old.’’ The commenter
further takes issue with the use in the
model of 70 degrees Fahrenheit (F) as an
average temperature, asserting that
summer temperatures routinely exceed
that mark, and that it is ‘‘settled
science’’ that as temperatures rise, so do
VOC emissions. The commenter asserts
that EPA ‘‘cannot assume with a straight
face’’ that these tanks will only operate
at 70 degrees F, that the 70 degrees F
assumption is only valid for indoor,
climate-controlled situations, and that
MDE’s negative declaration should be
disapproved because the model was
improperly performed and did not
consider ‘‘current and realistic
temperature and climatic data.’’ Finally,
the commenter asserts that the model
should be run using ‘‘average climatic
data for each month.’’
Response 2: EPA disagrees with the
commenter’s assertions. First, the CTG
provides flexibility and does not require
a specific method for calculating VOC
emissions. The model rule language
provided in the CTG requires only that
‘‘emissions must be calculated using a
generally accepted model or calculation
methodology.’’ 4 The new source
performance standards of title 40 of the
Code of Federal Regulations (CFR) part
60, subpart OOOOa, (also applying to
the oil and natural gas sector) include
similar language. See 40 CFR
60.5395a(a)(3). E&P TANKS is a
‘‘generally accepted’’ model, and
therefore an appropriate tool for
calculating VOC emissions for the
purpose of this negative declaration. In
fact, the model was one of the resources
utilized by EPA in the development of
4 See section A.2(i) of Model Rule Language; 2016
Oil and Gas CTG; Appendix A at A–8.
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the CTG.5 Second, while EPA
acknowledges that ambient
temperatures impact VOC emissions
from storage vessels, we do not agree
that the assumption of 70 degrees F as
an average temperature within the
model is inappropriate. Furthermore,
contrary to the commenter’s assertion,
the use of 70 degrees as an average is
not an assumption that the tank will
never operate above that temperature.
MDE identified six facilities that had
tanks potentially subject to the CTG: the
Dominion Cove Point LNG facility, the
Dominion Myersville compressor
station, the Enbridge Eastern Accident
compressor station, the Enbridge
Accident underground storage facility,
the Williams Transco Ellicott City
compressor station, and the
TransCanada compressor station. The
documentation provided by MDE
included submittals from the potentially
impacted sources, including the results
of TANKS modelling to evaluate their
particular storage vessels. Of the six
facilities identified, only the Dominion
facilities appear to have run the model
with an ‘‘across the board’’ assumption
of 70 degrees as the ambient
temperature.6 See attachments A–D of
MDE’s June 18, 2020 submittal.
Temperature data from the National
Weather Service for the Baltimore 7 area
for 2020 show that only three months—
June, July and August—exceeded an
average monthly temperature of 70
degrees (75.1, 82.6, and 78.7 degrees,
respectively).8 The other nine months
were below 70. Using 70 degrees as an
average for all twelve months is
therefore a conservative approach, as
the over-estimating for nine months
offsets the potential under-estimating
for the other three. Furthermore,
Dominion reported emissions for six
tanks, five at the Cove Point facility, and
one at the Myersville compressor
station. Of those tanks, only one
reported any emissions at all. That tank,
a 38,152 gallon tank, containing
‘‘hydrocarbons,’’ reported emissions of
only 0.02 tpy AND is equipped with a
control device (emissions are piped via
a closed loop to a flare). See Attachment
A of MDE’s June 18, 2020 submittal. The
modelling for the Enbridge tanks, as
5 See
2016 Oil and Gas CTG at 4–3.
submittal did not include documentation
for the modelling runs at the TransCanada
compressor station. Rather, an email from the
company to MDE indicated that they performed
TANKS modelling on four tanks, with a total
emission estimate across all units of 0.66 tpy. See
attachment D of MDE’s June 18, 2020 submittal.
7 Data for the Cove Point area was not
immediately available, but Baltimore is close
enough to provide a representative example.
8 See https://www.weather.gov/media/lwx/
climate/bwitemps.pdf
6 MDE’s
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52995
well as the Williams Transco tanks,
appears to have taken into account daily
temperature variations and other
variables to calculate actual monthly
averages. See Attachments B and C of
MDE’s June 18, 2020 submittal. This
approach, which is in line with the
commenter’s assertion, also results in
emissions that, in all cases, are well
below the 6 tpy threshold. We find these
analyses (and MDE’s reliance upon
them) to be reasonable. Therefore, we
disagree with the commenter and are
finalizing our approval of Maryland’s
negative declaration.
Comment 3: The commenter asserts
that EPA must disapprove MDE’s
negative declaration because ‘‘the
standards are not scientific or related to
scientific procedures and are not
consistent with the state’s development
priorities for air, water, and noise.’’
Further, the commenter asserts that the
SIP is not consistent with EPA’s ‘‘study
on methane emissions from drilling
operations,’’ that the guidelines ‘‘cannot
be promulgated under the state’s
authority’’ because they were ‘‘derived
from an out-of-date methodology used
in 2012,’’ and that MDE’s own review of
‘‘EPA’s 2012 study of hydraulic
fracturing fluid emissions’’ identified a
number of concerns about the findings.
Response 3: EPA disagrees with the
commenter’s assertion that we must
disapprove MDE’s June 18, 2020
submittal. First, the commenter makes
several references to ‘‘hydraulic
fracturing’’ (fracking), but none of the
wells addressed by MDE’s submittal
employ fracking as a means of
extraction. Indeed, Maryland has
imposed a ‘‘fracking ban,’’ and does not
allow the practice within the State. See
Md. Code Ann. Environment section
14–107.1. Therefore, fracking plays no
role in MDE’s negative declaration or
EPA’s approval. Second, it is not
entirely clear to which allegedly out of
date ‘‘methodology’’ and allegedly
unscientific ‘‘standards’’ the commenter
is referring. If the commenter is referring
to the CTG itself, the validity of the CTG
is not at issue in this action and will not
be addressed here. This action relates
only to MDE’s certification that there are
no sources within the State subject to
the CTG. The commenter has not
identified any flaws specific to MDE’s
methodology for making that
determination, nor with EPA’s proposed
approval. Therefore, we disagree with
the commenter and are finalizing our
approval of Maryland’s negative
declaration.
IV. Final Action
EPA is approving Maryland’s negative
declaration as a revision to Maryland’s
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SIP, to address the CAA requirements of
section 182(b)(2)(A) and 184(b)(1)(B)
under the 2008 and 2015 ozone
NAAQS, as they pertain to the 2016 Oil
and Gas CTG.
V. Statutory and Executive Order
Reviews
A. General Requirements
Under the CAA, the Administrator is
required to approve a SIP submission
that complies with the provisions of the
CAA and applicable Federal regulations.
42 U.S.C. 7410(k); 40 CFR 52.02(a).
Thus, in reviewing SIP submissions,
EPA’s role is to approve state choices,
provided that they meet the criteria of
the CAA. Accordingly, this action
merely approves state law as meeting
Federal requirements and does not
impose additional requirements beyond
those imposed by state law. For that
reason, this action:
• Is not a ‘‘significant regulatory
action’’ subject to review by the Office
of Management and Budget under
Executive Orders 12866 (58 FR 51735,
October 4, 1993) and 13563 (76 FR 3821,
January 21, 2011);
• Does not impose an information
collection burden under the provisions
of the Paperwork Reduction Act (44
U.S.C. 3501 et seq.);
• Is certified as not having a
significant economic impact on a
substantial number of small entities
under the Regulatory Flexibility Act (5
U.S.C. 601 et seq.);
• Does not contain any unfunded
mandate or significantly or uniquely
affect small governments, as described
in the Unfunded Mandates Reform Act
of 1995 (Pub. L. 104–4);
• Does not have federalism
implications as specified in Executive
Order 13132 (64 FR 43255, August 10,
1999);
• Is not an economically significant
regulatory action based on health or
safety risks subject to Executive Order
13045 (62 FR 19885, April 23, 1997);
Name of
non-regulatory
SIP revision
• Is not a significant regulatory action
subject to Executive Order 13211 (66 FR
28355, May 22, 2001);
• Is not subject to requirements of
section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (15 U.S.C. 272 note) because
application of those requirements would
be inconsistent with the CAA; and
• Does not provide EPA with the
discretionary authority to address, as
appropriate, disproportionate human
health or environmental effects, using
practicable and legally permissible
methods, under Executive Order 12898
(59 FR 7629, February 16, 1994).
In addition, this rule does not have
tribal implications as specified by
Executive Order 13175 (65 FR 67249,
November 9, 2000), because the SIP is
not approved to apply in Indian country
located in the State, and EPA notes that
it will not impose substantial direct
costs on tribal governments or preempt
tribal law.
B. Submission to Congress and the
Comptroller General
*
This action pertaining to Maryland’s
negative declaration for the 2016 Oil
and Gas CTG may not be challenged
later in proceedings to enforce its
requirements. (See section 307(b)(2).)
List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Incorporation by
reference, Ozone,Volatile organic
compounds.
Dated: September 15, 2021.
Diana Esher,
Acting Regional Administrator, Region III.
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. EPA will submit a
report containing this action 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).
For the reasons stated in the
preamble, the EPA amends 40 CFR part
52 as follows:
C. Petitions for Judicial Review
§ 52.1070
Under section 307(b)(1) of the CAA,
petitions for judicial review of this
*
Applicable
geographic
area
Negative Declaration for the 2016
Oil and Gas
CTG.
action must be filed in the United States
Court of Appeals for the appropriate
circuit by November 23, 2021. Filing a
petition for reconsideration by the
Administrator of this final rule does not
affect the finality of this action 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.
State
submittal
date
*
Statewide ........................................
*
6/18/20
PART 52—APPROVAL AND
PROMULGATION OF
IMPLEMENTATION PLANS
1. The authority citation for part 52
continues to read as follows:
■
Authority: 42 U.S.C. 7401 et seq.
Subpart V—Maryland
2. In § 52.1070, the table in paragraph
(e) is amended by adding the entry
‘‘Negative Declaration for the 2016 Oil
and Gas CTG’’ at the end of the table to
read as follows:
■
*
Identification of plan.
*
Additional explanation
*
*
9/24/21, [insert Federal Register
citation].
*
*
Negative declaration submitted for the 2008 and
2015 ozone national ambient air quality standards.
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EPA approval date
[FR Doc. 2021–20494 Filed 9–23–21; 8:45 am]
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(e) * * *
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Agencies
[Federal Register Volume 86, Number 183 (Friday, September 24, 2021)]
[Rules and Regulations]
[Pages 52993-52996]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2021-20494]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R03-OAR-2020-0528; FRL-8974-02-R3]
Air Plan Approval; Maryland; Negative Declaration for the Oil and
Gas Industry
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA) is approving a state
implementation plan (SIP) revision submitted by the State of Maryland.
This revision provides Maryland's determination, via a negative
declaration, that there are no sources within its borders subject to
EPA's 2016 Oil and Natural Gas control techniques guidelines (2016 Oil
and Gas CTG). EPA is approving these revisions to the Maryland SIP in
accordance with the requirements of the Clean Air Act (CAA).
DATES: This final rule is effective on October 25, 2021.
ADDRESSES: EPA has established a docket for this action under Docket ID
Number EPA-R03-OAR-2020-0528. All documents in the docket are listed on
the https://www.regulations.gov website. Although listed in the index,
some information is not publicly available, e.g., confidential business
information (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 through
https://www.regulations.gov, or please contact the person identified in
the FOR FURTHER INFORMATION CONTACT section for additional availability
information.
FOR FURTHER INFORMATION CONTACT: David Talley, Planning &
Implementation Branch (3AD30), Air & Radiation Division, U.S.
Environmental Protection Agency, Region III, 1650 Arch Street,
Philadelphia, Pennsylvania 19103. The telephone number is (215) 814-
2117. Mr. Talley can also be reached via electronic mail at
[email protected].
SUPPLEMENTARY INFORMATION:
I. Background
On February 9, 2021 (86 FR 8742), EPA published a notice of
proposed rulemaking (NPRM) for the State of Maryland. In the NPRM, EPA
proposed approval of Maryland's negative declaration SIP submittal for
the 2016 Oil and Gas CTG. On June 18, 2020, the Maryland Department of
the Environment (MDE) submitted the negative declaration for the 2016
Oil and Gas CTG as a revision to the Maryland SIP.
The CAA regulates emissions of nitrogen oxides (NOX) and
volatile organic compounds (VOCs) to prevent photochemical reactions
that result in ozone formation. Reasonably available control technology
(RACT) is a strategy for reducing NOX and VOC emissions from
stationary sources within designated nonattainment areas classified as
moderate or above that are not meeting the national ambient air quality
standards (NAAQS) for ozone. EPA has consistently defined ``RACT'' as
the lowest emission limit that a particular source is capable of
meeting by the application of the control technology that is reasonably
available considering technological and economic feasibility.
Control techniques guidelines (CTGs) and alternative control
techniques (ACTs) form important components of the guidance that EPA
provides to states for making RACT determinations. CTGs are used to
presumptively define VOC RACT for applicable source categories. CAA
section 182(b)(2)(A) requires that for ozone nonattainment areas
classified as moderate or above, states must revise their SIPs to
include provisions to implement RACT for each category of VOC sources
covered by a CTG document. CAA section 184(b)(1)(B) extends the RACT
obligation to all areas of states within the ozone transport region
(OTR), including Maryland.
[[Page 52994]]
States subject to RACT requirements are required to enact controls
for sources subject to CTGs that are at least as stringent as those
found within the CTG, either via the adoption of regulations or by
issuance of single source permits that outline what the source is
required to do to meet RACT. On March 6, 2016 (80 FR 12264), EPA issued
a final rule entitled ``Implementation of the 2008 National Ambient Air
Quality Standards for Ozone: State Implementation Plan Requirements''
(2008 Ozone Implementation Rule). In the preamble to the final rule,
EPA makes clear that if there are no sources covered by a specific CTG
source category located in an ozone nonattainment area or an area in
the OTR, the state may submit a negative declaration for that CTG. See
80 FR 12264, 12278. The same negative declaration is allowed by the
2015 ozone NAAQS implementation rule.\1\
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\1\ The majority of the provisions for implementing the 2008
ozone NAAQS (including those related to negative declarations) were
retained without revision for purposes of implementing the 2015
ozone NAAQS. See ``Implementation of the 2015 National Ambient Air
Quality Standards for Ozone: Nonattainment Area State Implementation
Plan Requirements'' (2015 Ozone Implementation Rule) 83 FR 62998
(December 6, 2018); and 40 CFR 51.1301.
---------------------------------------------------------------------------
On October 27, 2016 (81 FR 74798), EPA published in the Federal
Register the ``Release of Final Control Techniques Guidelines for the
Oil and Natural Gas Industry,'' (2016 Oil and Gas CTG). This CTG
provided information to state, local, and tribal air agencies to assist
in determining RACT for VOC emissions from certain VOC emission sources
within the oil and natural gas industry. The 2016 Oil and Gas CTG
replaces an earlier 1983 CTG entitled ``Control of Volatile Organic
Compound Equipment Leaks from Natural Gas/Gasoline Processing Plants.
December 1983.'' EPA-450/3-83-007 (1983 CTG) 49 FR 4432; February 6,
1984. See 2016 Oil and Gas CTG, p. 8-1.
II. Summary of SIP Revision and EPA Analysis
According to Maryland's June 18, 2020 submittal, MDE conducted a
review of potential sources subject to the 2016 Oil and Gas CTG. This
review consisted of a search of Maryland's oil and gas well records,
air permit records, EPA greenhouse gas reporting records, and the
Standard Industrial Classification (SIC) system. MDE's search
identified a total of 13 facilities in Maryland operating in the
production, processing, or transmission and storage segments of the oil
and natural gas industry. However, none of these facilities had storage
tanks or production wells that met or exceeded the applicability
criteria of the CTG. MDE identified five facilities in the natural gas
transmission sector, but determined that none of them had storage tanks
with the potential to emit (PTE) more than 6 tons per year (tpy) of
VOCs, which is the threshold for applicability of the CTG.\2\
Additionally, MDE identified eight active individual production wells,
but determined that none of these exceeded the 15 barrel equivalents
per day per well, which is the threshold for CTG applicability.\3\
Other specific requirements of the 2016 Oil and Gas CTG and the
rationale for EPA's proposed action are explained in the NPRM and will
not be restated here.
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\2\ See 2016 Oil and Gas CTG at 3-6.
\3\ See Id. at 3-7.
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III. EPA's Response to Comments Received
EPA received four sets of comments on our proposed approval of
Maryland's
June 18, 2020 negative declaration SIP submittal. One comment was
generally in favor of EPA's proposed action and will not be addressed
in this action. A summary of the other comments and EPA's response is
provided herein. All comments received are included in the docket for
this action.
Comment 1: The commenter asserts that the tanks and production
wells identified by MDE as being potentially subject to the CTG, but
determined by MDE to not meet the applicability thresholds and
therefore not subject to the 2016 Oil and Gas CTG, should have
mechanisms to limit their PTE to ensure that they remain below the
thresholds. The commenter provides the example of synthetic minor
permits. The commenter further asserts that relying on emission factors
or other engineering estimates would be arbitrary given the ``many
variables involved.''
Response 1: EPA disagrees with the commenter's assertions. First,
AP42 emissions factors and the engineering estimates (i.e. modelling)
relied upon in Maryland's submittal are generally accepted and are used
regularly in place of direct emissions measurement. Therefore, MDE's
reliance upon them for the purposes of this negative declaration is not
``arbitrary.'' EPA further disagrees with the commenter's assertion
that the reported facilities should have synthetic minor permits or
other enforceable limits on their PTE, and that it is ``implausible''
to claim that these facilities could have PTEs below the applicability
thresholds absent such limits. In support of this claim, the commenter
offers merely the ``many variables involved,'' such as varying
composition of the gas over time. EPA's review of Maryland's submittal
shows that the referenced sources all report emissions well below the
thresholds. For the potentially affected storage vessels (tanks),
Maryland provided extensive documentation, including calculations that
considered ambient temperature variations, throughput, and chemical
composition of the liquids stored in the tanks. All emissions reported
were considerably under the applicability threshold for storage
vessels. For example, of the six potentially affected tanks identified
at the Dominion Cove Point facility, the highest emissions reported
were 0.02 tpy of VOC, which is significantly below the 6 tpy threshold.
See Attachment A of MDE's June 18, 2020 submittal. The overwhelming
majority of the tanks analyzed reported emissions of only a fraction of
a ton per year. The highest reported emissions were for the two
condensate storage tanks at the Accident compressor station. Each of
those had calculated emissions of 1.2 tpy, still well below the
threshold. See Attachment B of MDE's June 18, 2020 submittal.
Similarly, EPA disagrees that the identified production wells need
enforceable limits on their production. First, the commenter has
provided no evidence to contradict MDE's evaluation of the wells'
outputs. Second, MDE certified in their submittal that their evaluation
of the production wells was based on a search of their permit records.
Each of the listed wells was constructed under a permit issued by
Maryland. MDE is therefore well positioned to review the data
associated with each of those permits and make an accurate
determination of each well's output. EPA finds no reason to determine
that MDE's determination with respect to the wells was unreasonable.
EPA believes that there is a sufficient margin between the reported
emissions and the applicability threshold to determine that the
identified sources do not need enforceable PTE limits in order for EPA
to approve Maryland's negative declaration. Furthermore, Federal
regulations are only necessary if a covered source exceeds the
applicability thresholds established by the CTG. Maryland has certified
that none of the sources within its jurisdiction exceed these
thresholds. Should any of the reported sources exceed the thresholds in
the future; or should a new source of the type covered by the existing
CTG emitting more than either threshold be constructed in the state
after approval of a negative declaration, EPA expects the
[[Page 52995]]
state to develop a regulation and submit it to EPA for approval into
the SIP in accordance with the relevant timing provided for by the CAA.
Additionally, it is likely that any significant change in the operation
of the existing facilities which would impact their PTE would be
subject to preconstruction review by MDE. The same is true for the
construction of new sources. At this time, because Maryland does not
have any sources subject to the 2016 Oil and Gas CTG, no regulation is
required to be developed and submitted for EPA approval. Therefore, we
disagree with the commenter and are finalizing our approval of
Maryland's negative declaration.
Comment 2: The commenter asserts that EPA should disapprove MDE's
June 18, 2020 submittal because it relies on TANKS modelling, which
utilizes outdated information, including temperature/climate data which
is ``all over 10 years old.'' The commenter further takes issue with
the use in the model of 70 degrees Fahrenheit (F) as an average
temperature, asserting that summer temperatures routinely exceed that
mark, and that it is ``settled science'' that as temperatures rise, so
do VOC emissions. The commenter asserts that EPA ``cannot assume with a
straight face'' that these tanks will only operate at 70 degrees F,
that the 70 degrees F assumption is only valid for indoor, climate-
controlled situations, and that MDE's negative declaration should be
disapproved because the model was improperly performed and did not
consider ``current and realistic temperature and climatic data.''
Finally, the commenter asserts that the model should be run using
``average climatic data for each month.''
Response 2: EPA disagrees with the commenter's assertions. First,
the CTG provides flexibility and does not require a specific method for
calculating VOC emissions. The model rule language provided in the CTG
requires only that ``emissions must be calculated using a generally
accepted model or calculation methodology.'' \4\ The new source
performance standards of title 40 of the Code of Federal Regulations
(CFR) part 60, subpart OOOOa, (also applying to the oil and natural gas
sector) include similar language. See 40 CFR 60.5395a(a)(3). E&P TANKS
is a ``generally accepted'' model, and therefore an appropriate tool
for calculating VOC emissions for the purpose of this negative
declaration. In fact, the model was one of the resources utilized by
EPA in the development of the CTG.\5\ Second, while EPA acknowledges
that ambient temperatures impact VOC emissions from storage vessels, we
do not agree that the assumption of 70 degrees F as an average
temperature within the model is inappropriate. Furthermore, contrary to
the commenter's assertion, the use of 70 degrees as an average is not
an assumption that the tank will never operate above that temperature.
MDE identified six facilities that had tanks potentially subject to the
CTG: the Dominion Cove Point LNG facility, the Dominion Myersville
compressor station, the Enbridge Eastern Accident compressor station,
the Enbridge Accident underground storage facility, the Williams
Transco Ellicott City compressor station, and the TransCanada
compressor station. The documentation provided by MDE included
submittals from the potentially impacted sources, including the results
of TANKS modelling to evaluate their particular storage vessels. Of the
six facilities identified, only the Dominion facilities appear to have
run the model with an ``across the board'' assumption of 70 degrees as
the ambient temperature.\6\ See attachments A-D of MDE's June 18, 2020
submittal. Temperature data from the National Weather Service for the
Baltimore \7\ area for 2020 show that only three months--June, July and
August--exceeded an average monthly temperature of 70 degrees (75.1,
82.6, and 78.7 degrees, respectively).\8\ The other nine months were
below 70. Using 70 degrees as an average for all twelve months is
therefore a conservative approach, as the over-estimating for nine
months offsets the potential under-estimating for the other three.
Furthermore, Dominion reported emissions for six tanks, five at the
Cove Point facility, and one at the Myersville compressor station. Of
those tanks, only one reported any emissions at all. That tank, a
38,152 gallon tank, containing ``hydrocarbons,'' reported emissions of
only 0.02 tpy AND is equipped with a control device (emissions are
piped via a closed loop to a flare). See Attachment A of MDE's June 18,
2020 submittal. The modelling for the Enbridge tanks, as well as the
Williams Transco tanks, appears to have taken into account daily
temperature variations and other variables to calculate actual monthly
averages. See Attachments B and C of MDE's June 18, 2020 submittal.
This approach, which is in line with the commenter's assertion, also
results in emissions that, in all cases, are well below the 6 tpy
threshold. We find these analyses (and MDE's reliance upon them) to be
reasonable. Therefore, we disagree with the commenter and are
finalizing our approval of Maryland's negative declaration.
---------------------------------------------------------------------------
\4\ See section A.2(i) of Model Rule Language; 2016 Oil and Gas
CTG; Appendix A at A-8.
\5\ See 2016 Oil and Gas CTG at 4-3.
\6\ MDE's submittal did not include documentation for the
modelling runs at the TransCanada compressor station. Rather, an
email from the company to MDE indicated that they performed TANKS
modelling on four tanks, with a total emission estimate across all
units of 0.66 tpy. See attachment D of MDE's June 18, 2020
submittal.
\7\ Data for the Cove Point area was not immediately available,
but Baltimore is close enough to provide a representative example.
\8\ See https://www.weather.gov/media/lwx/climate/bwitemps.pdf
---------------------------------------------------------------------------
Comment 3: The commenter asserts that EPA must disapprove MDE's
negative declaration because ``the standards are not scientific or
related to scientific procedures and are not consistent with the
state's development priorities for air, water, and noise.'' Further,
the commenter asserts that the SIP is not consistent with EPA's ``study
on methane emissions from drilling operations,'' that the guidelines
``cannot be promulgated under the state's authority'' because they were
``derived from an out-of-date methodology used in 2012,'' and that
MDE's own review of ``EPA's 2012 study of hydraulic fracturing fluid
emissions'' identified a number of concerns about the findings.
Response 3: EPA disagrees with the commenter's assertion that we
must disapprove MDE's June 18, 2020 submittal. First, the commenter
makes several references to ``hydraulic fracturing'' (fracking), but
none of the wells addressed by MDE's submittal employ fracking as a
means of extraction. Indeed, Maryland has imposed a ``fracking ban,''
and does not allow the practice within the State. See Md. Code Ann.
Environment section 14-107.1. Therefore, fracking plays no role in
MDE's negative declaration or EPA's approval. Second, it is not
entirely clear to which allegedly out of date ``methodology'' and
allegedly unscientific ``standards'' the commenter is referring. If the
commenter is referring to the CTG itself, the validity of the CTG is
not at issue in this action and will not be addressed here. This action
relates only to MDE's certification that there are no sources within
the State subject to the CTG. The commenter has not identified any
flaws specific to MDE's methodology for making that determination, nor
with EPA's proposed approval. Therefore, we disagree with the commenter
and are finalizing our approval of Maryland's negative declaration.
IV. Final Action
EPA is approving Maryland's negative declaration as a revision to
Maryland's
[[Page 52996]]
SIP, to address the CAA requirements of section 182(b)(2)(A) and
184(b)(1)(B) under the 2008 and 2015 ozone NAAQS, as they pertain to
the 2016 Oil and Gas CTG.
V. Statutory and Executive Order Reviews
A. General Requirements
Under the CAA, the Administrator is required to approve a SIP
submission that complies with the provisions of the CAA and applicable
Federal regulations. 42 U.S.C. 7410(k); 40 CFR 52.02(a). Thus, in
reviewing SIP submissions, EPA's role is to approve state choices,
provided that they meet the criteria of the CAA. Accordingly, this
action merely approves state law as meeting Federal requirements and
does not impose additional requirements beyond those imposed by state
law. For that reason, this action:
Is not a ``significant regulatory action'' subject to
review by the Office of Management and Budget under Executive Orders
12866 (58 FR 51735, October 4, 1993) and 13563 (76 FR 3821, January 21,
2011);
Does not impose an information collection burden under the
provisions of the Paperwork Reduction Act (44 U.S.C. 3501 et seq.);
Is certified as not having a significant economic impact
on a substantial number of small entities under the Regulatory
Flexibility Act (5 U.S.C. 601 et seq.);
Does not contain any unfunded mandate or significantly or
uniquely affect small governments, as described in the Unfunded
Mandates Reform Act of 1995 (Pub. L. 104-4);
Does not have federalism implications as specified in
Executive Order 13132 (64 FR 43255, August 10, 1999);
Is not an economically significant regulatory action based
on health or safety risks subject to Executive Order 13045 (62 FR
19885, April 23, 1997);
Is not a significant regulatory action subject to
Executive Order 13211 (66 FR 28355, May 22, 2001);
Is not subject to requirements of section 12(d) of the
National Technology Transfer and Advancement Act of 1995 (15 U.S.C. 272
note) because application of those requirements would be inconsistent
with the CAA; and
Does not provide EPA with the discretionary authority to
address, as appropriate, disproportionate human health or environmental
effects, using practicable and legally permissible methods, under
Executive Order 12898 (59 FR 7629, February 16, 1994).
In addition, this rule does not have tribal implications as
specified by Executive Order 13175 (65 FR 67249, November 9, 2000),
because the SIP is not approved to apply in Indian country located in
the State, and EPA notes that it will not impose substantial direct
costs on tribal governments or preempt tribal law.
B. Submission to Congress and the Comptroller General
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. EPA will submit a report containing this action 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).
C. Petitions for Judicial Review
Under section 307(b)(1) of the CAA, petitions for judicial review
of this action must be filed in the United States Court of Appeals for
the appropriate circuit by November 23, 2021. Filing a petition for
reconsideration by the Administrator of this final rule does not affect
the finality of this action 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.
This action pertaining to Maryland's negative declaration for the
2016 Oil and Gas CTG may not be challenged later in proceedings to
enforce its requirements. (See section 307(b)(2).)
List of Subjects in 40 CFR Part 52
Environmental protection, Air pollution control, Incorporation by
reference, Ozone,Volatile organic compounds.
Dated: September 15, 2021.
Diana Esher,
Acting Regional Administrator, Region III.
For the reasons stated in the preamble, the EPA amends 40 CFR part
52 as follows:
PART 52--APPROVAL AND PROMULGATION OF IMPLEMENTATION PLANS
0
1. The authority citation for part 52 continues to read as follows:
Authority: 42 U.S.C. 7401 et seq.
Subpart V--Maryland
0
2. In Sec. 52.1070, the table in paragraph (e) is amended by adding
the entry ``Negative Declaration for the 2016 Oil and Gas CTG'' at the
end of the table to read as follows:
Sec. 52.1070 Identification of plan.
* * * * *
(e) * * *
----------------------------------------------------------------------------------------------------------------
State
Name of non-regulatory SIP Applicable geographic submittal EPA approval date Additional explanation
revision area date
----------------------------------------------------------------------------------------------------------------
* * * * * * *
Negative Declaration for Statewide............. 6/18/20 9/24/21, [insert Negative declaration
the 2016 Oil and Gas CTG. Federal Register submitted for the
citation]. 2008 and 2015 ozone
national ambient air
quality standards.
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[FR Doc. 2021-20494 Filed 9-23-21; 8:45 am]
BILLING CODE 6560-50-P