Notice of Final Approval for an Alternative Means of Emission Limitation at ExxonMobil Corporation; Marathon Petroleum Company, LP (for Itself and on Behalf of Its Subsidiary, Blanchard Refining, LLC); Chalmette Refining, LLC; and LACC, LLC, 46939-46945 [2018-20148]
Download as PDF
Federal Register / Vol. 83, No. 180 / Monday, September 17, 2018 / Notices
of the protest or intervention to the
Federal Energy Regulatory Commission,
888 First Street NE, Washington, DC
20426.
This filing is accessible on-line at
https://www.ferc.gov, using the eLibrary
link and is available for electronic
review in the Commission’s Public
Reference Room in Washington, DC.
There is an eSubscription link on the
website that enables subscribers to
receive email notification when a
document is added to a subscribed
docket(s). For assistance with any FERC
Online service, please email
FERCOnlineSupport@ferc.gov, or call
(866) 208–3676 (toll free). For TTY, call
(202) 502–8659.
Comment Date: 5:00 p.m. Eastern
Time on September 28, 2018.
Dated: September 11, 2018.
Kimberly D. Bose,
Secretary.
[FR Doc. 2018–20101 Filed 9–14–18; 8:45 am]
BILLING CODE 6717–01–P
ENVIRONMENTAL PROTECTION
AGENCY
[EPA–HQ–OAR–2014–0738 and EPA–HQ–
OAR–2010–0682; FRL–9983–26–OAR]
Notice of Final Approval for an
Alternative Means of Emission
Limitation at ExxonMobil Corporation;
Marathon Petroleum Company, LP (for
Itself and on Behalf of Its Subsidiary,
Blanchard Refining, LLC); Chalmette
Refining, LLC; and LACC, LLC
Environmental Protection
Agency (EPA).
ACTION: Notice; final approval.
AGENCY:
This notice announces our
approval of the Alternative Means of
Emission Limitation (AMEL) requests
under the Clean Air Act (CAA)
submitted from ExxonMobil
Corporation; Marathon Petroleum
Company, LP (for itself and on behalf of
its subsidiary, Blanchard Refining, LLC);
and Chalmette Refining, LLC to operate
flares and multi-point ground flares
(MPGFs) at several refineries in Texas
and Louisiana, and from LACC, LLC to
operate flares at a chemical plant in
Louisiana. This approval notice
specifies the operating conditions and
monitoring, recordkeeping, and
reporting requirements that these
facilities must follow to demonstrate
compliance with the approved AMEL.
DATES: The approval of the AMEL
requests from ExxonMobil Corporation;
Marathon Petroleum Company, LP (for
itself and on behalf of its subsidiary,
Blanchard Refining, LLC); Chalmette
daltland on DSKBBV9HB2PROD with NOTICES
SUMMARY:
VerDate Sep<11>2014
17:47 Sep 14, 2018
Jkt 244001
Refining, LLC; and LACC, LLC to
operate certain flares at the refineries
and a chemical plant, as specified in
this notice, is effective on September 17,
2018.
ADDRESSES: The Environmental
Protection Agency (EPA) has established
a docket for this action under Docket ID
No. EPA–HQ–OAR–2014–0738. All
documents in the docket are listed on
the https://www.regulations.gov
website. Although listed, 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 either electronically through
https://www.regulations.gov or in hard
copy at EPA Docket Center, EPA WJC
West Building, Room Number 3334,
1301 Constitution Ave. NW,
Washington, DC. The Public Reading
Room hours of operation are 8:30 a.m.
to 4:30 p.m. Eastern Standard Time
(EST), Monday through Friday. The
telephone number for the Public
Reading Room is (202) 566–1744, and
the telephone number for the Docket
Center is (202) 566–1742.
FOR FURTHER INFORMATION CONTACT: For
questions about this final action, contact
Ms. Angie Carey, Sector Policies and
Programs Division (E143–01), Office of
Air Quality Planning and Standards,
U.S. Environmental Protection Agency,
Research Triangle Park, North Carolina
27711; telephone number: (919) 541–
2187; fax number: (919) 541–0516; and
email address: carey.angela@epa.gov.
SUPPLEMENTARY INFORMATION: Preamble
acronyms and abbreviations. We use
multiple acronyms and terms in this
preamble. While this list may not be
exhaustive, to ease the reading of this
preamble and for reference purposes,
the EPA defines the following terms and
acronyms here:
AMEL alternative means of emission
limitation
BTU/scf British thermal units per standard
cubic foot
CAA Clean Air Act
CBI confidential business information
CFR Code of Federal Regulations
EPA Environmental Protection Agency
Eqn equation
g/mol grams per gram mole
HAP hazardous air pollutants
HP high pressure
LFL lower flammability limit
LFLcz lower flammability limit of
combustion zone gas
LFLvg lower flammability limit of flare vent
gas
PO 00000
Frm 00030
Fmt 4703
Sfmt 4703
46939
LRGO linear relief gas oxidizer
MPGF multi-point ground flare
NESHAP national emission standards for
hazardous air pollutants
NHV net heating value
NHVcz net heating value of combustion
zone gas
NHVvg net heating value of flare vent gas
NSPS new source performance standards
OAQPS Office of Air Quality Planning and
Standards
scf standard cubic feet
SKEC steam-assisted kinetic energy
combustor
TCEQ Texas Commission on Environmental
Quality
VOC volatile organic compounds
Organization of This Document. The
information in this notice is organized
as follows:
I. Background
A. Summary
B. Regulatory Flare Requirements
II. Summary of Public Comments on the
AMEL Requests
III. AMEL for the Flares
I. Background
A. Summary
In a Federal Register notice dated
April 25, 2018, the EPA provided public
notice and solicited comment on the
requests under the CAA from
ExxonMobil Corporation; Marathon
Petroleum Company, LP (for itself and
on behalf of its subsidiary, Blanchard
Refining, LLC’s); and Chalmette
Refining, LLC for the operation of flares
and MPGFs at several refineries in
Texas and Louisiana, and from LACC,
LLC to operate flares at a chemical plant
in Louisiana (see 83 FR 18034). This
action solicited comment on all aspects
of the AMEL requests, including the
operating conditions specified in that
action that are necessary to achieve a
reduction in emissions of volatile
organic compounds and organic
hazardous air pollutants at least
equivalent to the reduction in emissions
required by various standards in 40 CFR
parts 60, 61, and 63 that apply to
emission sources that would be
controlled by these flares and MPGFs.
These standards incorporate the flare
design and operating requirements in 40
CFR part 60 and 63 General Provisions
(i.e., 40 CFR 60.18(b) and 63.11(b)) into
the individual new source performance
standards (NSPS) and maximum
achievable control technology (MACT)
subparts, except for the Petroleum
Refinery MACT, 40 CFR part 63, subpart
CC, which specifies its flare
requirements within the subpart (i.e., 40
CFR 63.670). Four of the requests are for
flares located at petroleum refineries,
while the request from LACC, LLC is for
a flare design at a chemical
manufacturing facility. None of the
E:\FR\FM\17SEN1.SGM
17SEN1
46940
Federal Register / Vol. 83, No. 180 / Monday, September 17, 2018 / Notices
flares located at petroleum refineries
can meet the flare tip velocity limits in
the Petroleum Refinery MACT, 40 CFR
part 63, subpart CC. In addition, flares
at these refineries and at LACC’s
chemical plant that are subject to other
40 CFR part 60 and 63 standards cannot
meet the flare tip velocity limits
contained in the applicable General
Provisions to 40 CFR part 60 and 63.
This action provides a summary of the
comments received as part of the public
review process, our response to those
comments, and our approval of these
AMEL requests.
B. Regulatory Flare Requirements
ExxonMobil, Marathon, Blanchard,
and Chalmette provided the information
specified in the flare AMEL framework
set forth in the Petroleum Refinery
MACT at 40 CFR 63.670(r) to support
their AMEL requests. LACC provided
the information specified in the flare
AMEL framework finalized on April 21,
2016 (81 FR 23486), to support its
AMEL request. The ExxonMobil
Corporation Baytown Refinery in
Baytown, Texas, is seeking an AMEL to
operate a gas-assisted flare, Flare 26,
during periods of startup, shutdown,
upsets, and emergency events, as well as
during fuel gas imbalance events.
Marathon Petroleum Company, LP’s
Garyville, Louisiana Refinery, and
Blanchard Refining, LLC’s Galveston
Bay Refinery (GBR) in Texas City,
Texas, are seeking AMELs to operate
their flares only during periods of
startup, shutdown, upsets, and
emergency events. Chalmette Refining,
LLC in Chalmette, Louisiana, is seeking
an AMEL to operate its flare, No. 1
Flare, during periods of upset and
emergency events. LACC, LLC is seeking
an AMEL to operate flares at its
chemical plant in Lake Charles,
Louisiana, during startups, shutdowns,
upsets, and emergency events. See Table
1 for a list of regulations, by subparts,
that each refinery and chemical plant
has identified as applicable to the flares
described above.
TABLE 1—SUMMARY OF APPLICABLE RULES THAT MAY APPLY TO STREAMS CONTROLLED BY FLARES
Applicable rules
with vent
streams going to
control device(s)
Exxon Mobil
Baytown,
Texas
Flare 26
Marathon
Garyville,
LA MPGF
Blanchard
Refining
GBR MPGF
Chalmette
No. 1 Flare
LACC
Rule citation from title 40 CFR
that allow for use of a flare
Provisions for alternative means
of emission limitation
NSPS Subpart VV ....
NSPS Subpart VVa ..
NSPS Subpart NNN
NSPS Subpart QQQ
NSPS Subpart RRR
NSPS Subpart Kb ....
NESHAP Subpart V
....................
....................
....................
....................
....................
....................
....................
x
x
x
x
x
x
x
x
x
x
x
x
x
x
....................
....................
x
....................
....................
....................
....................
................
x
x
................
x
x
x
60.482–10(d) ................................
60.482–10a(d) ..............................
60.662(b) ......................................
60.692–5(c) ..................................
60.702(b) ......................................
60.112b(a)(3)(ii) ...........................
61.242–11(d) ................................
NESHAP Subpart J ..
....................
....................
....................
....................
x
61.242–11(d) ................................
NESHAP Subpart Y
....................
x
x
....................
................
61.271–(c)(2) ...............................
NESHAP Subpart BB
....................
x
x
....................
................
61.302(c) ......................................
NESHAP Subpart FF
NESHAP Subpart F
NESHAP Subpart G
....................
....................
....................
x
x
x
x
x
x
....................
....................
....................
x
x
x
NESHAP
NESHAP
NESHAP
NESHAP
NESHAP
....................
....................
x
....................
....................
x
x
x
....................
....................
x
x
x
....................
....................
....................
....................
x
....................
....................
x
x
................
x
x
....................
x
x
....................
................
61.349(a)(2) .................................
63.103(a) ......................................
63.113(a)(1)(i), 63.116(a)(2),
63.116(a)(3), 63.119(e),
63.120(e)(1) through (4),
63.126(b)(2)(i), 63.128(b),
63.139(c)(3), 63.139(d)(3),
63.145(j).
63.172(d), 63.180(e) ....................
63.982(b) ......................................
63.643(a)(1) .................................
63.1034 ........................................
Table 7 to 63.1103(e) cross-references to NESHAP subpart
SS above.
63.2378(a),63.2382, 63.2398 ......
60.484(a)–(f).
60.484a(a)–(f).
CAA section 111(h)(3).
42 U.S.C. 7411(h)(3).
CAA section 111(h)(3).
60.114b.
40 CFR 63.6(g); 42 U.S.C.
7412(h)(3).
40 CFR 63.6(g); 42 U.S.C.
7412(h)(3).
40 CFR 63.6(g); 40 CFR 61.273;
42 U.S.C. 7412(h)(3).
40 CFR 63.6(g); 42 U.S.C.
7412(h)(3).
61.353(a); also see 61.12(d).
63.6(g); 42 U.S.C. 7412(h)(3).
63.6(g); 42 U.S.C. 7412(h)(3).
Subpart
Subpart
Subpart
Subpart
Subpart
daltland on DSKBBV9HB2PROD with NOTICES
NESHAP Subpart
EEEE.
H
SS
CC
UU
YY
The provisions for the NSPS and
National Emission Standards for
Hazardous Air Pollutants (NESHAP)
cited in Table 1 that ensure flares meet
certain specific requirements when used
to satisfy the requirements of the NSPS
or NESHAP were established as work
practice standards pursuant to CAA
sections 111(h)(1) or 112(h)(1). For
standards established according to these
provisions, CAA sections 111(h)(3) and
112(h)(3) allow the EPA to permit the
use of an AMEL by a source if, after
VerDate Sep<11>2014
17:47 Sep 14, 2018
Jkt 244001
notice and opportunity for comment,1 it
is established to the Administrator’s
satisfaction that such an AMEL will
achieve emission reductions at least
equivalent to the reductions required
under the CAA section 111(h)(1) or
112(h)(1) standard. As noted in Table 1,
many of the NSPS and NESHAP in the
table above also include specific
1 CAA section 111(h)(3) specifically requires that
the EPA provide an opportunity for a public
hearing. The EPA provided an opportunity for a
public hearing in the April 25, 2018, Federal
Register action. However, no public hearing was
requested.
PO 00000
Frm 00031
Fmt 4703
Sfmt 4703
63.177; 42 U.S.C. 7412(h)(3).
CAA section 112(h)(3).
63.670(r).
63.1021(a)–(d).
63.1113.
63.6(g); 42 U.S.C. 7412(h)(3).
regulatory provisions allowing sources
to request an AMEL.
II. Summary of Public Comments on the
AMEL Requests
The EPA received four public
comments on this action. Specifically,
the EPA received suggested changes and
clarifications from LACC, LLC,
Marathon Petroleum Company, LP (for
itself and on behalf of its subsidiary,
Blanchard Refining, LLC), and
ExxonMobil Corporation. The EPA also
received one comment that does not
mention any of the AMEL requests at
issue and is, therefore, outside the scope
E:\FR\FM\17SEN1.SGM
17SEN1
daltland on DSKBBV9HB2PROD with NOTICES
Federal Register / Vol. 83, No. 180 / Monday, September 17, 2018 / Notices
of the action. As discussed in more
detail below, we have modified or
otherwise clarified certain operating
conditions in response to comments.2
All of the comments within the scope of
the AMEL requests were supportive of
the EPA approving the AMEL requests,
and none of the comments raised issues
with the EPA’s authority to approve
these AMEL requests under the CAA.
None of the commenters asserted that
the EPA lacked authority to approve the
AMEL requests or that the AMEL
requests would not achieve at least
equivalent emissions reductions as
flares that meet the standards in the
General Provisions or in the Petroleum
Refinery MACT at 40 CFR 63.670(r).
Comment: LACC, LLC commented
that the monitoring requirement in
section (3) to install a video camera
capable of continuously recording (i.e.,
at least one frame every 15 seconds with
time and date stamps) images of the
flare flame at a reasonable distance and
suitable angle, will work for their
MPGF, but not for their enclosed ground
flare. LACC stated that it is not
technically feasible to install a video
camera and monitor the flare flame
within the enclosed ground flare.
Alternatively, LACC stated that it can
monitor for the presence of visible
emissions from the enclosed ground
flare by using a video camera to monitor
at the exit of the stack exhaust.
Response: We agree that, although the
camera would not be able to directly
monitor visible emissions from the flare
flame because of the enclosure,
conducting visible emissions
observations at the stack would be a
reliable indicator of compliance with
the requirements in section (3) below.
Therefore, we accept this alternative
and have made the appropriate change
in section (3) below.
Comment: Marathon Petroleum
Company, LP commented that the
operating conditions in Table 2 do not
reflect what they requested in their
AMEL for the MPGF at their Garyville
refinery. They stated that they needed
separate NHVcz limits for the pressureassisted linear relief gas oxidizers
(LRGO burners) and the steam-assisted
steam kinetic energy combustors (SKEC
burners) when both are being used
simultaneously. Marathon explained
that the SKEC burners would have a
considerably different NHVcz value
because of steam assist. This is because
the steam assist is included in the
NHVcz calculation for the SKEC burners,
2 As explained below, we have clarified the
reporting requirements for Exxon’s Flare 26 in
response to a comment by Exxon. We have similarly
clarified Marathon’s Garyville’s and GBR’s MPGFs
reporting requirements as a result of this comment.
VerDate Sep<11>2014
17:47 Sep 14, 2018
Jkt 244001
but not for the LRGO burners, given that
the LRGO burners do not have steam
assist.
Response: The EPA acknowledges
that the April notice did not reflect
Marathon Petroleum Company, LP’s
supplemental request for the Garyville
MPGF to maintain separate burner
limits such that the SKEC burners
would meet the NHVcz target from the
SKEC equation and the LRGO burners
would meet 600 British thermal units
per standard cubic feet (BTU/scf). We
discussed with Marathon its
supplemental request upon receiving
the comment. As we explained in that
discussion, based on our review of the
information provided by Marathon, the
steam-to-vent gas ratio for the SKEC
burners is not high enough to
significantly affect the NHVcz during the
high pressure flaring scenario.
Therefore, we conclude that the burner
requirements as set out in the April 25,
2018, AMEL document are appropriate.
Marathon concurred with this
conclusion in an email response after
the comment period closed (available in
Docket ID No. EPA–HQ–OAR–2014–
0738 and EPA–HQ–OAR–2010–0682).
Comment: Marathon Petroleum
Company, LP commented that the
requirement should be NHVvg = NHVcz
with a limit of ≥600 BTU/scf for the LH
burner, and NHVcz ≥600 BTU/scf for
LRGO burners. Marathon notes that, as
explained in its February 2, 2018, and
March 27, 2018, supplemental letters,
since the LH burner is air-assisted,
therefore, the LH burner limitations
provided in its request correspond to
the NHVvg and not the NHVcz. Marathon
further notes that the Petroleum
Refinery requirements at 40 CFR
63.670(m)(1) states that NHVvg = NHVcz
when there is no premix assist air flow.
Response: For the reasons provided in
Marathon’s comment, we agree that for
the LH burner, which is perimeter air
assisted and not pre-mix air assisted, the
NHVvg equals NHVcz. We, therefore,
made this change in Table 2 below.
Comment: ExxonMobil Corporation
commented on a typographical
correction in Table 2 for the Baytown,
Texas, Flexicoker Flare 26. The
proposed alternative operating
condition was listed as ≥270 BTU/scf
NHVcz and velocity of <361 feet per
second (ft/sec). However, the
performance test results for the Flare 26
demonstrate that the destruction
efficiency met 98 percent at 361 ft/sec.
Response: We accept this correction
and made the change in Table 2 to ≤361
ft/sec.
Comment: ExxonMobil Corporation
commented that the EPA should include
a default molecular weight for pipeline
PO 00000
Frm 00032
Fmt 4703
Sfmt 4703
46941
natural gas that corresponds to an
NHV of 920 BTU/scf listed in 40 CFR
63.670(j)(5).
Response: We agree and are
specifying the molecular weight of
pipeline natural gas as 16.85 grams per
gram mole (g/mol). It would be
burdensome for Exxon to take samples
of natural gas to determine molecular
weight, when very little changes in
molecular weight are expected.
Therefore, we are specifying the
molecular weight of natural gas of 16.85
can be used. This molecular weight is
based on our default natural gas
composition that was used to determine
the net heating value in 40 CFR 63.670.
Comment: ExxonMobil Corporation
commented that the accuracy and
calibration requirements in section (1)(f)
of the initial Federal Register document
should apply only to flares at chemical
plants seeking AMEL approval since
flares such as Exxon’s Flare 26 is
already subject to the accuracy and
calibration requirements in the
Petroleum Refinery MACT at 40 CFR
63.671(a)(1) and (4) and Table 13.
Response: We agree and have clarified
in section (1)(f) below that the accuracy
and calibration requirements listed in
Table 4 do not apply to refinery flares
subject to requirements at 40 CFR
63.671(a)(1) and (4) and Table 13 of 40
CFR part 63, subpart CC.
Comment: ExxonMobil Corporation
commented that the Flare 26 follows the
Petroleum Refinery MACT requirement
at 40 CFR part 63, subpart CC, for pilot
flame operations and does not use crosslighting for the flare operation. They
stated that the EPA should clarify in
section (2) that the Flare 26 is only
required to maintain flare pilots per the
Petroleum Refinery MACT requirements
in 40 CFR 63.670(b).
Response: We agree that the
requirements in section (2), which apply
to flares that cross light, should not
apply to Flare 26 because it does not use
cross-lighting. We have made this
change in section (2) below.
Comment: ExxonMobil Corporation
commented that the EPA should clarify
which reporting requirements apply to
the Flare 26 in section (6) and clarify
that the reporting requirements for the
flare tip velocity and NHVcz are
applicable when regulated material is
routed to the flare for at least 15
minutes.
Response: While we believe that the
records required in section (6)(c) are
essentially the same as the reporting
requirements in Petroleum Refinery
NESHAP, 40 CFR part 63, subpart CC,
section (6)(c) requires additional records
related to the operation of MPGFs,
which do not apply to Flare 26. Further,
E:\FR\FM\17SEN1.SGM
17SEN1
46942
Federal Register / Vol. 83, No. 180 / Monday, September 17, 2018 / Notices
we agree that the operating limits for
NHVcz and Vtip apply whenever
regulated material is routed to the flares
for at least 15 minutes, as specified by
40 CFR part 63, subpart CC; Therefore,
we are requiring that Flare 26 comply
with the reporting requirements in the
Petroleum Refinery NESHAP, 40 CFR
part 63, subpart CC, instead of section
(6) as part of this AMEL approval.
However, MPGFs located at petroleum
refineries must comply with the
additional reporting requirements for
MPGFs in (6)(c)(iv) and (v). To avoid
other potential confusion, we are
clarifying the applicability of section
(6)(c) to all the flares covered in this
notice. Specifically, section (6)(c) below
provides that flares at refineries must
meet the requirements in the Petroleum
Refinery MACT in 40 CFR
63.655(g)(11)(i)–(iii), except that the
applicable alternative operating
conditions listed in Table 2 apply
instead of the operating limits specified
in 40 CFR 63.670(d) through (f). In
addition, for refinery flares that are
MPGFs, notification shall also include
records specified in section (6)(c)(iv)–
(v). For LACC MPGFs, the notification
shall include the records specified in
section (6)(c)(i)–(v).
III. AMEL for the Flares
Based upon our review of the AMEL
requests and the comments received
through the public comment period, we
are approving these AMEL requests and
are establishing operating conditions for
the flares at issue. The AMEL and the
associated operating conditions are
specified in Table 2 and accompanying
paragraphs. These operating conditions
will ensure that these flares will achieve
emission reductions at least equivalent
to flares complying with the flare
requirements under the applicable
NESHAP and NSPS identified in
Table 1.
TABLE 2—ALTERNATIVE OPERATING CONDITIONS
AMEL
submitted
Company
Affected facilities
Flare type(s)
11/7/17 ...........
ExxonMobil ............
Elevated gas-assist
flare.
≥270 BTU/scf NHVcz and velocity ≤361 (ft/sec).
10/7/17 ...........
Marathon ................
Baytown, TX
Flexicoker Flare
26.
Garyville, LA ..........
2 MPGFs ................
10/7/17 ...........
9/19/17 ...........
Marathon/Blanchard
Refining.
Chalmette Refining
GBR (Texas City,
TX).
Chalmette, LA ........
When both SKEC and LRGO burners are being used, the
higher of ≥600 BTU/scf NHVcz or ≥127.27 ln(vvg)¥110.87
NHVcz. When only the SKEC burner is being used
≥127.27 ln(vvg)¥110.87 NHVcz.
NHVvg ≥600 BTU/scf for the LH burner, and NHVcz ≥600
BTU/scf for LRGO burners.
≥1,000 BTU/scf NHVcz or LFLcz ≤6.5 vol%.
5/1/17 .............
LACC .....................
Lake Charles, LA ...
VerDate Sep<11>2014
17:47 Sep 14, 2018
Jkt 244001
≥1075 BTU/scf NHVcz for INDAIR Burners; ≥800 BTU/scf
NHVcz for LRGO only.
(ii) If the owner or operator uses a
continuous net heating value monitor,
the owner or operator may, at their
discretion, install, operate, calibrate,
and maintain a monitoring system
capable of continuously measuring,
calculating, and recording the hydrogen
concentration in the flare vent gas. The
owner or operator shall use the
following equation to determine NHVvg
for each sample measured via the net
heating value monitoring system.
PO 00000
Frm 00033
Fmt 4703
Sfmt 4703
Where:
NHVvg = Net heating value of flare vent gas,
BTU/scf.
NHVmeasured = Net heating value of flare vent
gas stream as measured by the
continuous net heating value monitoring
system, BTU/scf.
xH2 = Concentration of hydrogen in flare vent
gas at the time the sample was input into
the net heating value monitoring system,
volume fraction.
938 = Net correction for the measured
heating value of hydrogen (1,212 ¥274),
BTU/scf.
(iii) For non-assisted flare burners,
and the GBR LH burner, NHVvg =
NHVcz. For assisted burners, such as the
Marathon Garyville MPGF SKEC
burners, and the Exxon Flare 26 gasassisted burner, NHVcz is calculated
using Equation 3.
Where:
NHVcz = Net heating value of combustion
E:\FR\FM\17SEN1.SGM
17SEN1
EN17SE18.004
gas), flare sweep gas, flare purge gas, and
flare supplemental gas, but does not
include pilot gas.
i = Individual component in flare vent gas.
n = Number of components in flare vent gas.
xi = Concentration of component i in flare
vent gas, volume fraction.
NHVi = Net heating value of component i
determined as the heat of combustion
where the net enthalpy per mole of
offgas is based on combustion at 25
degrees Celsius (°C) and 1 atmosphere
(or constant pressure) with water in the
gaseous state from values published in
the literature, and then the values
converted to a volumetric basis using 20
°C for ‘‘standard temperature.’’ Table 3
summarizes component properties
including net heating values.
EN17SE18.003
Where:
NHVvg = Net heating value of flare vent gas,
BTU/scf. Flare vent gas means all gas
found just prior to the tip. This gas
includes all flare waste gas (i.e., gas from
facility operations that is directed to a
flare for the purpose of disposing the
Elevated multi-point
flare.
2 MPGFs ...............
EN17SE18.002
daltland on DSKBBV9HB2PROD with NOTICES
(1) All flares must be operated such
that the combustion zone gas net
heating value (NHVcz) or the lower
flammability in the combustion zone
(LFLcz) as specified in Table 2 is met.
Owners or operators must demonstrate
compliance with the applicable NHVcz
or LFLcz specified in Table 2 on a 15minute block average. Owners or
operators must calculate and monitor
for the NHVcz or LFLcz according to the
following:
(a) Calculation of NHVcz
(i) If an owner or operator elects to
use a monitoring system capable of
continuously measuring (i.e., at least
once every 15 minutes), calculating, and
recording the individual component
concentrations present in the flare vent
gas, NHVvg shall be calculated using the
following equation:
MPGF ....................
Alternative operating conditions
46943
Federal Register / Vol. 83, No. 180 / Monday, September 17, 2018 / Notices
zone gas, BTU/scf.
NHVvg = Net heating value of flare vent gas
for the 15-minute block period as
determined according to (1)(a)(i), BTU/
scf.
Qvg = Cumulative volumetric flow of flare
vent gas during the 15-minute block
period, scf.
Qag = Cumulative volumetric flow of assist
gas during the 15-minute block period,
scf flow rate, scf.
NHVag = Net heating value of assist gas, BTU/
scf; this is zero for air or for steam.
(ii) For non-assisted flare burners,
LFLvg = LFLcz.
(c) Calculation of Vtip
For the ExxonMobil Flare 26, the
owner or operator shall calculate the 15minute block average Vtip by using the
following equation:
(b) Calculation of LFLcz
(i) The owner or operator shall
determine LFLcz from compositional
analysis data by using the following
equation:
Where:
Vtip = Flare tip velocity, ft/sec.
Qvg = Cumulative volumetric flow of vent gas
over 15-minute block average period, scf.
Area = Unobstructed area of the flare tip,
square ft.
900 = Conversion factor, seconds per 15minute block average.
Where:
LFLvg = Lower flammability limit of flare vent
gas, volume percent (vol %).
n = Number of components in the vent gas.
i = Individual component in the vent gas.
ci = Concentration of component i in the vent
gas, vol %.
LFLi = Lower flammability limit of
component i as determined using values
published by the U.S. Bureau of Mines
(Zabetakis, 1965), vol %. All inerts,
including nitrogen, are assumed to have
an infinite LFL (e.g., LFLN2 = ∞, so that
cN2/LFLN2 = 0). LFL values for common
flare vent gas components are provided
in Table 3.
(d) For all flare systems specified in
this document, the owner or operator
shall install, operate, calibrate, and
maintain a monitoring system capable of
continuously measuring the volumetric
flow rate of flare vent gas (Qvg), the
volumetric flow rate of total assist steam
(Qs), the volumetric flow rate of total
assist air (Qa), and the volumetric flow
rate of total assist gas (Qag).
(i) The flow rate monitoring systems
must be able to correct for the
temperature and pressure of the system
and output parameters in standard
conditions (i.e., a temperature of 20 °C
(68 °F) and a pressure of 1 atmosphere).
(ii) Mass flow monitors may be used
for determining volumetric flow rate of
flare vent gas provided the molecular
weight of the flare vent gas is
determined using compositional
analysis so that the mass flow rate can
be converted to volumetric flow at
standard conditions using the following
equation:
Where:
Qvol = Volumetric flow rate, scf/sec.
Qmass = Mass flow rate, pounds per sec.
385.3 = Conversion factor, scf per poundmole.
MWt = Molecular weight of the gas at the
flow monitoring location, pounds per poundmole.
(e) For each measurement produced
by the monitoring system used to
comply with (1)(a)(ii), the operator shall
determine the 15-minute block average
as the arithmetic average of all
measurements made by the monitoring
system within the 15-minute period.
(f) The owner or operator must follow
the accuracy and calibration procedures
according to Table 4. Flares at refineries
must meet the accuracy and calibration
requirements in the Petroleum Refinery
MACT at 40 CFR 63.671(a)(1) and (4)
and Table 13. Maintenance periods,
instrument adjustments, or checks to
maintain precision and accuracy and
zero and span adjustments may not
exceed 5 percent of the time the flare is
receiving regulated material.
Acetylene .........................................................................................................
Benzene ...........................................................................................................
1,2-Butadiene ..................................................................................................
1,3-Butadiene ..................................................................................................
iso-Butane ........................................................................................................
n-Butane ..........................................................................................................
cis-Butene ........................................................................................................
iso-Butene ........................................................................................................
trans-Butene ....................................................................................................
Carbon Dioxide ................................................................................................
Carbon Monoxide ............................................................................................
Cyclopropane ...................................................................................................
Ethane .............................................................................................................
Ethylene ...........................................................................................................
Hydrogen .........................................................................................................
Hydrogen Sulfide .............................................................................................
Methane ...........................................................................................................
Methyl-Acetylene .............................................................................................
Nitrogen ...........................................................................................................
Oxygen ............................................................................................................
Pentane+ (C5+) ...............................................................................................
Propadiene ......................................................................................................
Propane ...........................................................................................................
Propylene .........................................................................................................
C2H2 ..............
C6H6 ..............
C4H6 ..............
C4H6 ..............
C4H10 .............
C4H10 .............
C4H8 ..............
C4H8 ..............
C4H8 ..............
CO2 ................
CO .................
C3H6 ..............
C2H6 ..............
C2H4 ..............
H2 ...................
H2S ................
CH4 ................
C3H4 ..............
N2 ...................
O2 ..................
C5H12 .............
C3H4 ..............
C3H8 ..............
C3H6 ..............
VerDate Sep<11>2014
17:47 Sep 14, 2018
Jkt 244001
PO 00000
Frm 00034
Fmt 4703
Sfmt 4703
MWi
(pounds per
pound-mole)
E:\FR\FM\17SEN1.SGM
26.04
78.11
54.09
54.09
58.12
58.12
56.11
56.11
56.11
44.01
28.01
42.08
30.07
28.05
2.02
34.08
16.04
40.06
28.01
32.00
72.15
40.06
44.10
42.08
17SEN1
NHVi
(BTU/scf)
1,404
3,591
2,794
2,690
2,957
2,968
2,830
2,928
2,826
0
316
2,185
1,595
1,477
* 1,212
587
896
2,088
0
0
3,655
2,066
2,281
2,150
LFLi
(volume %)
2.5
1.3
2.0
2.0
1.8
1.8
1.6
1.8
1.7
∞
12.5
2.4
3.0
2.7
4.0
4.0
5.0
1.7
∞
∞
1.4
2.16
2.1
2.4
EN17SE18.007
Molecular
formula
EN17SE18.006
Component
EN17SE18.005
daltland on DSKBBV9HB2PROD with NOTICES
TABLE 3—INDIVIDUAL COMPONENT PROPERTIES
46944
Federal Register / Vol. 83, No. 180 / Monday, September 17, 2018 / Notices
TABLE 3—INDIVIDUAL COMPONENT PROPERTIES—Continued
Component
Molecular
formula
Water ...............................................................................................................
H2O ................
MWi
(pounds per
pound-mole)
NHVi
(BTU/scf)
18.02
LFLi
(volume %)
0
∞
* The theoretical net heating value for hydrogen is 274 BTU/scf, but for the purposes of the flare requirement in this subpart, a net heating
value of 1,212 BTU/scf shall be used.
TABLE 4—ACCURACY AND CALIBRATION REQUIREMENTS
Parameter
Accuracy requirements
Calibration requirements
Flare Vent Gas Flow Rate
±20 percent of flow rate at velocities ranging from 0.1
to 1 foot per second.
±5 percent of flow rate at velocities greater than 1
foot per second.
Flow Rate for All Flows
Other Than Flare Vent
Gas.
±5 percent over the normal range of flow measured
or 1.9 liters per minute (0.5 gallons per minute),
whichever is greater, for liquid flow.
Performance evaluation biennially (every 2 years) and following any period of
more than 24 hours throughout which the flow rate exceeded the maximum
rated flow rate of the sensor, or the data recorder was off scale. Checks of all
mechanical connections for leakage monthly. Visual inspections and checks
of system operation every 3 months, unless the system has a redundant flow
sensor.
Select a representative measurement location where swirling flow or abnormal
velocity distributions due to upstream and downstream disturbances at the
point of measurement are minimized.
Conduct a flow sensor calibration check at least biennially (every 2 years); conduct a calibration check following any period of more than 24 hours throughout which the flow rate exceeded the manufacturer’s specified maximum rated
flow rate or install a new flow sensor.
At least quarterly, inspect all components for leakage, unless the continuous parameter monitoring system (CPMS) has a redundant flow sensor.
daltland on DSKBBV9HB2PROD with NOTICES
±5 percent over the normal range of flow measured
or 280 liters per minute (10 cubic feet per minute),
whichever is greater, for gas flow.
±5 percent over the normal range measured for mass
flow.
Pressure ............................
±5 percent over the normal range measured or 0.12
kilopascals (0.5 inches of water column), whichever is greater.
Net Heating Value by Calorimeter.
±2 percent of span .......................................................
Net Heating Value by Gas
Chromatograph.
As specified in Performance Standard (PS) 9 of 40
CFR part 60, appendix B.
Hydrogen Analyzer ............
±2 percent over the concentration measured, or 0.1
volume, percent, whichever is greater.
(2) The flare system shall be operated
with a flame present at all times when
in use. Additionally, each stage that
cross-lights must have at least two pilots
with a continuously lit pilot flame,
except for Chalmette’s No. 1 Flare,
which has one pilot for each stage,
excluding stages 8A and 8B. Each pilot
flame must be continuously monitored
by a thermocouple or any other
VerDate Sep<11>2014
17:47 Sep 14, 2018
Jkt 244001
Record the results of each calibration check and inspection.
Locate the flow sensor(s) and other necessary equipment (such as straightening
vanes) in a position that provides representative flow; reduce swirling flow or
abnormal velocity distributions due to upstream and downstream disturbances.
Review pressure sensor readings at least once a week for straight-line (unchanging) pressure and perform corrective action to ensure proper pressure
sensor operation if blockage is indicated.
Performance evaluation annually and following any period of more than 24
hours throughout which the pressure exceeded the maximum rated pressure
of the sensor, or the data recorder was off scale. Checks of all mechanical
connections for leakage monthly. Visual inspection of all components for integrity, oxidation, and galvanic corrosion every 3 months, unless the system
has a redundant pressure sensor.
Select a representative measurement location that minimizes or eliminates pulsating pressure, vibration, and internal and external corrosion.
Calibration requirements—follow manufacturer’s recommendations at a minimum.
Temperature control (heated and/or cooled as necessary) the sampling system
to ensure proper year-round operation.
Where feasible, select a sampling location at least 2 equivalent diameters
downstream from and 0.5 equivalent diameters upstream from the nearest
disturbance. Select the sampling location at least 2 equivalent duct diameters
from the nearest control device, point of pollutant generation, air in-leakages,
or other point at which a change in the pollutant concentration or emission
rate occurs.
Follow the procedure in PS 9 of 40 CFR part 60, appendix B, except that a single daily mid-level calibration check can be used (rather than triplicate analysis), the multi-point calibration can be conducted quarterly (rather than
monthly), and the sampling line temperature must be maintained at a minimum temperature of 60 °C (rather than 120 °C).
Specify calibration requirements in your site specific CPMS monitoring plan.
Calibration requirements—follow manufacturer’s recommendations at a minimum.
Specify the sampling location at least 2 equivalent duct diameters from the
nearest control device, point of pollutant generation, air in-leakages, or other
point at which a change in the pollutant concentration occurs.
equivalent device used to detect the
presence of a flame. The time, date, and
duration of any complete loss of pilot
flame on any of the burners must be
recorded. Each monitoring device must
be maintained or replaced at a
frequency in accordance with the
manufacturer’s specifications. The
ExxonMobil flare, Flare 26, and GBR’s
LH flare must meet the requirements in
PO 00000
Frm 00035
Fmt 4703
Sfmt 4703
the Petroleum Refinery MACT at 40 CFR
63.670(b) instead of the requirements
herein in section (2).
(3) Flares at refineries shall comply
with the Petroleum Refinery MACT
requirements of 40 CFR 63.670(h). For
LACC, LLC’s MPGFs, the flare system
shall be operated with no visible
emissions except for periods not to
exceed a total of 5 minutes during any
E:\FR\FM\17SEN1.SGM
17SEN1
daltland on DSKBBV9HB2PROD with NOTICES
Federal Register / Vol. 83, No. 180 / Monday, September 17, 2018 / Notices
2 consecutive hours. A video camera
that is capable of continuously
recording (i.e., at least one frame every
15 seconds with time and date stamps)
images of the flare flame and a
reasonable distance above the flare
flame at an angle suitable for visible
emissions observations must be used to
demonstrate compliance with this
requirement. For LACC’s enclosed
ground flare, LACC must install a video
camera that is capable of continuously
recording (i.e., at least one frame every
15 seconds with time and date stamps)
the stack exhaust exit at a reasonable
distance and at an angle suitable for
visible emissions observation in order to
demonstrate compliance with this
requirement. The owner or operator
must provide real-time video
surveillance camera output to the
control room or other continuously
manned location where the video
camera images may be viewed at any
time.
(4) For the MPGFs and Chalmette’s
No. 1 Flare, the owner or operator of a
flare system shall install and operate
pressure monitor(s) on the main flare
header, as well as a valve position
indicator monitoring system capable of
monitoring and recording the position
for each staging valve to ensure that the
flare operates within the range of tested
conditions or within the range of the
manufacturer’s specifications. Flares at
refineries must meet the accuracy and
calibration requirements in the
Petroleum Refinery MACT at 40 CFR
63.671(a)(1) and (4) and Table 13. The
pressure monitor at LACC shall meet the
accuracy and calibration requirements
in Table 4. Maintenance periods,
instrument adjustments or checks to
maintain precision and accuracy, and
zero and span adjustments may not
exceed 5 percent of the time the flare is
receiving regulated material.
(5) Recordkeeping Requirements
(a) All data must be recorded and
maintained for a minimum of 3 years or
for as long as required under applicable
rule subpart(s), whichever is longer.
(6) Reporting Requirements
(a) The information specified in
section III(6)(b) and (c) below must be
reported in the timeline specified by the
applicable rule subpart(s) for which the
flare will control emissions.
(b) Owners or operators shall include
the final AMEL operating requirements
for each flare in their initial Notification
of Compliance status report.
(c) The owner or operator shall notify
the Administrator of periods of excess
emissions in their Periodic Reports. The
owner or operator of refinery flares shall
meet the reporting requirements in the
Petroleum Refinery MACT in 40 CFR
VerDate Sep<11>2014
17:47 Sep 14, 2018
Jkt 244001
63.655(g)(11)(i)–(iii), except that the
applicable alternative operating
conditions listed in Table 2 apply
instead of the operating limits specified
in 40 CFR 63.670(d) through (f). In
addition, for refinery flares that are
MPGFs, notification shall also include
records specified in section (iv)–(v)
below. For LACC MPGFs, the
notification shall include the records
specified in section (i)–(v) below.
(i) Records of each 15-minute block
for all flares during which there was at
least 1 minute when regulated material
was routed to the flare and a complete
loss of pilot flame on a stage of burners
occurred, and for all flares, records of
each 15-minute block during which
there was at least 1 minute when
regulated material was routed to the
flare and a complete loss of pilot flame
on an individual burner occurred.
(ii) Records of visible emissions
events (including the time and date
stamp) that exceed more than 5 minutes
in any 2-hour consecutive period.
(iii) Records of each 15-minute block
period for which an applicable
combustion zone operating condition
(i.e., NHVcz or LFLcz) is not met for the
flare when regulated material is being
combusted in the flare. Indicate the date
and time for each period, the NHVcz
and/or LFLcz operating parameter for the
period, the type of monitoring system
used to determine compliance with the
operating parameters (e.g., gas
chromatograph or calorimeter), and also
indicate which high-pressure stages
were in use.
(iv) Records of when the pressure
monitor(s) on the main flare header
show the flare burners are operating
outside the range of tested conditions or
outside the range of the manufacturer’s
specifications. Indicate the date and
time for each period, the pressure
measurement, the stage(s) and number
of flare burners affected, and the range
of tested conditions or manufacturer’s
specifications.
(v) Records of when the staging valve
position indicator monitoring system
indicates a stage of the flare should not
be in operation and is or when a stage
of the flare should be in operation and
is not. Indicate the date and time for
each period, whether the stage was
supposed to be open, but was closed, or
vice versa, and the stage(s) and number
of flare burners affected.
Dated: September 11, 2018.
Panagiotis Tsirigotis,
Director, Office of Air Quality Planning and
Standards.
[FR Doc. 2018–20148 Filed 9–14–18; 8:45 am]
BILLING CODE 6560–50–P
PO 00000
Frm 00036
Fmt 4703
Sfmt 4703
46945
ENVIRONMENTAL PROTECTION
AGENCY
[FRL–9983–85—Region 3]
Clean Water Act: West Virginia’s
NPDES Program Revision
Environmental Protection
Agency (EPA).
ACTION: Notice of revision, public
comment period, and opportunity to
request a public hearing.
AGENCY:
The State of West Virginia has
submitted revisions to its authorized
National Pollutant Discharge
Elimination System (NPDES) program
for the U.S. Environmental Protection
Agency’s (EPA) review. These revisions
consist of amendments to the West
Virginia Water Pollution Control Act
codified in Senate Bill 357 (SB 357) and
to West Virginia’s Code of State
Regulations codified as House Bill 2283
(HB 2283). The EPA has determined that
the submitted revisions constitute a
substantial revision to West Virginia’s
authorized NPDES program.
Accordingly, the EPA is requesting
public comment and providing a notice
of an opportunity to request a public
hearing. Copies of SB357 and HB2283
are available for public inspection as
indicated below.
DATES: Comments must be submitted in
writing to EPA on or before October 17,
2018.
ADDRESSES: Comments on the WV
NPDES Program revisions should be
sent to Francisco Cruz, Water Protection
Division (3WP41), U.S. Environmental
Protection Agency Region 3, 1650 Arch
Street, Philadelphia, PA 19103–2019 or
email to cruz.francisco@epa.gov. Oral
comments will not be considered.
Underlying documents from the
administrative record for this decision
are available for public inspection at the
above address. Please contact Mr.
Francisco Cruz to schedule an
inspection. The public, during the term
of this Federal Register notice, can
request a public hearing. Such a hearing
will be held if there is significant public
interest based on requests received.
FOR FURTHER INFORMATION CONTACT: For
additional information, contact
Francisco Cruz at (215) 814–5734.
SUPPLEMENTARY INFORMATION: Section
402 of the Federal Clean Water Act
(CWA) created the NPDES program
under which the EPA may issue permits
for the discharge of pollutants into
waters of the United States under
conditions required by the CWA.
Section 402(b) allows states to assume
NPDES program responsibilities upon
approval by the EPA. On May 10, 1982,
SUMMARY:
E:\FR\FM\17SEN1.SGM
17SEN1
Agencies
[Federal Register Volume 83, Number 180 (Monday, September 17, 2018)]
[Notices]
[Pages 46939-46945]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2018-20148]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
[EPA-HQ-OAR-2014-0738 and EPA-HQ-OAR-2010-0682; FRL-9983-26-OAR]
Notice of Final Approval for an Alternative Means of Emission
Limitation at ExxonMobil Corporation; Marathon Petroleum Company, LP
(for Itself and on Behalf of Its Subsidiary, Blanchard Refining, LLC);
Chalmette Refining, LLC; and LACC, LLC
AGENCY: Environmental Protection Agency (EPA).
ACTION: Notice; final approval.
-----------------------------------------------------------------------
SUMMARY: This notice announces our approval of the Alternative Means of
Emission Limitation (AMEL) requests under the Clean Air Act (CAA)
submitted from ExxonMobil Corporation; Marathon Petroleum Company, LP
(for itself and on behalf of its subsidiary, Blanchard Refining, LLC);
and Chalmette Refining, LLC to operate flares and multi-point ground
flares (MPGFs) at several refineries in Texas and Louisiana, and from
LACC, LLC to operate flares at a chemical plant in Louisiana. This
approval notice specifies the operating conditions and monitoring,
recordkeeping, and reporting requirements that these facilities must
follow to demonstrate compliance with the approved AMEL.
DATES: The approval of the AMEL requests from ExxonMobil Corporation;
Marathon Petroleum Company, LP (for itself and on behalf of its
subsidiary, Blanchard Refining, LLC); Chalmette Refining, LLC; and
LACC, LLC to operate certain flares at the refineries and a chemical
plant, as specified in this notice, is effective on September 17, 2018.
ADDRESSES: The Environmental Protection Agency (EPA) has established a
docket for this action under Docket ID No. EPA-HQ-OAR-2014-0738. All
documents in the docket are listed on the https://www.regulations.gov
website. Although listed, 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 either electronically through https://www.regulations.gov or in hard copy at EPA Docket Center, EPA WJC West
Building, Room Number 3334, 1301 Constitution Ave. NW, Washington, DC.
The Public Reading Room hours of operation are 8:30 a.m. to 4:30 p.m.
Eastern Standard Time (EST), Monday through Friday. The telephone
number for the Public Reading Room is (202) 566-1744, and the telephone
number for the Docket Center is (202) 566-1742.
FOR FURTHER INFORMATION CONTACT: For questions about this final action,
contact Ms. Angie Carey, Sector Policies and Programs Division (E143-
01), Office of Air Quality Planning and Standards, U.S. Environmental
Protection Agency, Research Triangle Park, North Carolina 27711;
telephone number: (919) 541-2187; fax number: (919) 541-0516; and email
address: [email protected].
SUPPLEMENTARY INFORMATION: Preamble acronyms and abbreviations. We use
multiple acronyms and terms in this preamble. While this list may not
be exhaustive, to ease the reading of this preamble and for reference
purposes, the EPA defines the following terms and acronyms here:
AMEL alternative means of emission limitation
BTU/scf British thermal units per standard cubic foot
CAA Clean Air Act
CBI confidential business information
CFR Code of Federal Regulations
EPA Environmental Protection Agency
Eqn equation
g/mol grams per gram mole
HAP hazardous air pollutants
HP high pressure
LFL lower flammability limit
LFLcz lower flammability limit of combustion zone gas
LFLvg lower flammability limit of flare vent gas
LRGO linear relief gas oxidizer
MPGF multi-point ground flare
NESHAP national emission standards for hazardous air pollutants
NHV net heating value
NHVcz net heating value of combustion zone gas
NHVvg net heating value of flare vent gas
NSPS new source performance standards
OAQPS Office of Air Quality Planning and Standards
scf standard cubic feet
SKEC steam-assisted kinetic energy combustor
TCEQ Texas Commission on Environmental Quality
VOC volatile organic compounds
Organization of This Document. The information in this notice is
organized as follows:
I. Background
A. Summary
B. Regulatory Flare Requirements
II. Summary of Public Comments on the AMEL Requests
III. AMEL for the Flares
I. Background
A. Summary
In a Federal Register notice dated April 25, 2018, the EPA provided
public notice and solicited comment on the requests under the CAA from
ExxonMobil Corporation; Marathon Petroleum Company, LP (for itself and
on behalf of its subsidiary, Blanchard Refining, LLC's); and Chalmette
Refining, LLC for the operation of flares and MPGFs at several
refineries in Texas and Louisiana, and from LACC, LLC to operate flares
at a chemical plant in Louisiana (see 83 FR 18034). This action
solicited comment on all aspects of the AMEL requests, including the
operating conditions specified in that action that are necessary to
achieve a reduction in emissions of volatile organic compounds and
organic hazardous air pollutants at least equivalent to the reduction
in emissions required by various standards in 40 CFR parts 60, 61, and
63 that apply to emission sources that would be controlled by these
flares and MPGFs. These standards incorporate the flare design and
operating requirements in 40 CFR part 60 and 63 General Provisions
(i.e., 40 CFR 60.18(b) and 63.11(b)) into the individual new source
performance standards (NSPS) and maximum achievable control technology
(MACT) subparts, except for the Petroleum Refinery MACT, 40 CFR part
63, subpart CC, which specifies its flare requirements within the
subpart (i.e., 40 CFR 63.670). Four of the requests are for flares
located at petroleum refineries, while the request from LACC, LLC is
for a flare design at a chemical manufacturing facility. None of the
[[Page 46940]]
flares located at petroleum refineries can meet the flare tip velocity
limits in the Petroleum Refinery MACT, 40 CFR part 63, subpart CC. In
addition, flares at these refineries and at LACC's chemical plant that
are subject to other 40 CFR part 60 and 63 standards cannot meet the
flare tip velocity limits contained in the applicable General
Provisions to 40 CFR part 60 and 63.
This action provides a summary of the comments received as part of
the public review process, our response to those comments, and our
approval of these AMEL requests.
B. Regulatory Flare Requirements
ExxonMobil, Marathon, Blanchard, and Chalmette provided the
information specified in the flare AMEL framework set forth in the
Petroleum Refinery MACT at 40 CFR 63.670(r) to support their AMEL
requests. LACC provided the information specified in the flare AMEL
framework finalized on April 21, 2016 (81 FR 23486), to support its
AMEL request. The ExxonMobil Corporation Baytown Refinery in Baytown,
Texas, is seeking an AMEL to operate a gas-assisted flare, Flare 26,
during periods of startup, shutdown, upsets, and emergency events, as
well as during fuel gas imbalance events. Marathon Petroleum Company,
LP's Garyville, Louisiana Refinery, and Blanchard Refining, LLC's
Galveston Bay Refinery (GBR) in Texas City, Texas, are seeking AMELs to
operate their flares only during periods of startup, shutdown, upsets,
and emergency events. Chalmette Refining, LLC in Chalmette, Louisiana,
is seeking an AMEL to operate its flare, No. 1 Flare, during periods of
upset and emergency events. LACC, LLC is seeking an AMEL to operate
flares at its chemical plant in Lake Charles, Louisiana, during
startups, shutdowns, upsets, and emergency events. See Table 1 for a
list of regulations, by subparts, that each refinery and chemical plant
has identified as applicable to the flares described above.
Table 1--Summary of Applicable Rules That May Apply to Streams Controlled by Flares
--------------------------------------------------------------------------------------------------------------------------------------------------------
Exxon Mobil
Applicable rules with vent Baytown, Marathon Blanchard Chalmette Rule citation from title Provisions for
streams going to control Texas Flare Garyville, Refining GBR No. 1 Flare LACC 40 CFR that allow for alternative means of
device(s) 26 LA MPGF MPGF use of a flare emission limitation
--------------------------------------------------------------------------------------------------------------------------------------------------------
NSPS Subpart VV................. ............ x x ............ .......... 60.482-10(d)............ 60.484(a)-(f).
NSPS Subpart VVa................ ............ x x ............ x 60.482-10a(d)........... 60.484a(a)-(f).
NSPS Subpart NNN................ ............ x x x x 60.662(b)............... CAA section 111(h)(3).
NSPS Subpart QQQ................ ............ x x ............ .......... 60.692-5(c)............. 42 U.S.C. 7411(h)(3).
NSPS Subpart RRR................ ............ x x ............ x 60.702(b)............... CAA section 111(h)(3).
NSPS Subpart Kb................. ............ x x ............ x 60.112b(a)(3)(ii)....... 60.114b.
NESHAP Subpart V................ ............ x x ............ x 61.242-11(d)............ 40 CFR 63.6(g); 42
U.S.C. 7412(h)(3).
NESHAP Subpart J................ ............ ............ ............ ............ x 61.242-11(d)............ 40 CFR 63.6(g); 42
U.S.C. 7412(h)(3).
NESHAP Subpart Y................ ............ x x ............ .......... 61.271-(c)(2)........... 40 CFR 63.6(g); 40 CFR
61.273; 42 U.S.C.
7412(h)(3).
NESHAP Subpart BB............... ............ x x ............ .......... 61.302(c)............... 40 CFR 63.6(g); 42
U.S.C. 7412(h)(3).
NESHAP Subpart FF............... ............ x x ............ x 61.349(a)(2)............ 61.353(a); also see
61.12(d).
NESHAP Subpart F................ ............ x x ............ x 63.103(a)............... 63.6(g); 42 U.S.C.
7412(h)(3).
NESHAP Subpart G................ ............ x x ............ x 63.113(a)(1)(i), 63.6(g); 42 U.S.C.
63.116(a)(2), 7412(h)(3).
63.116(a)(3),
63.119(e), 63.120(e)(1)
through (4),
63.126(b)(2)(i),
63.128(b),
63.139(c)(3),
63.139(d)(3), 63.145(j).
NESHAP Subpart H................ ............ x x ............ x 63.172(d), 63.180(e).... 63.177; 42 U.S.C.
7412(h)(3).
NESHAP Subpart SS............... ............ x x ............ x 63.982(b)............... CAA section 112(h)(3).
NESHAP Subpart CC............... x x x x .......... 63.643(a)(1)............ 63.670(r).
NESHAP Subpart UU............... ............ ............ ............ ............ x 63.1034................. 63.1021(a)-(d).
NESHAP Subpart YY............... ............ ............ ............ ............ x Table 7 to 63.1103(e) 63.1113.
cross-references to
NESHAP subpart SS above.
NESHAP Subpart EEEE............. ............ x x ............ .......... 63.2378(a),63.2382, 63.6(g); 42 U.S.C.
63.2398. 7412(h)(3).
--------------------------------------------------------------------------------------------------------------------------------------------------------
The provisions for the NSPS and National Emission Standards for
Hazardous Air Pollutants (NESHAP) cited in Table 1 that ensure flares
meet certain specific requirements when used to satisfy the
requirements of the NSPS or NESHAP were established as work practice
standards pursuant to CAA sections 111(h)(1) or 112(h)(1). For
standards established according to these provisions, CAA sections
111(h)(3) and 112(h)(3) allow the EPA to permit the use of an AMEL by a
source if, after notice and opportunity for comment,\1\ it is
established to the Administrator's satisfaction that such an AMEL will
achieve emission reductions at least equivalent to the reductions
required under the CAA section 111(h)(1) or 112(h)(1) standard. As
noted in Table 1, many of the NSPS and NESHAP in the table above also
include specific regulatory provisions allowing sources to request an
AMEL.
---------------------------------------------------------------------------
\1\ CAA section 111(h)(3) specifically requires that the EPA
provide an opportunity for a public hearing. The EPA provided an
opportunity for a public hearing in the April 25, 2018, Federal
Register action. However, no public hearing was requested.
---------------------------------------------------------------------------
II. Summary of Public Comments on the AMEL Requests
The EPA received four public comments on this action. Specifically,
the EPA received suggested changes and clarifications from LACC, LLC,
Marathon Petroleum Company, LP (for itself and on behalf of its
subsidiary, Blanchard Refining, LLC), and ExxonMobil Corporation. The
EPA also received one comment that does not mention any of the AMEL
requests at issue and is, therefore, outside the scope
[[Page 46941]]
of the action. As discussed in more detail below, we have modified or
otherwise clarified certain operating conditions in response to
comments.\2\ All of the comments within the scope of the AMEL requests
were supportive of the EPA approving the AMEL requests, and none of the
comments raised issues with the EPA's authority to approve these AMEL
requests under the CAA. None of the commenters asserted that the EPA
lacked authority to approve the AMEL requests or that the AMEL requests
would not achieve at least equivalent emissions reductions as flares
that meet the standards in the General Provisions or in the Petroleum
Refinery MACT at 40 CFR 63.670(r).
---------------------------------------------------------------------------
\2\ As explained below, we have clarified the reporting
requirements for Exxon's Flare 26 in response to a comment by Exxon.
We have similarly clarified Marathon's Garyville's and GBR's MPGFs
reporting requirements as a result of this comment.
---------------------------------------------------------------------------
Comment: LACC, LLC commented that the monitoring requirement in
section (3) to install a video camera capable of continuously recording
(i.e., at least one frame every 15 seconds with time and date stamps)
images of the flare flame at a reasonable distance and suitable angle,
will work for their MPGF, but not for their enclosed ground flare. LACC
stated that it is not technically feasible to install a video camera
and monitor the flare flame within the enclosed ground flare.
Alternatively, LACC stated that it can monitor for the presence of
visible emissions from the enclosed ground flare by using a video
camera to monitor at the exit of the stack exhaust.
Response: We agree that, although the camera would not be able to
directly monitor visible emissions from the flare flame because of the
enclosure, conducting visible emissions observations at the stack would
be a reliable indicator of compliance with the requirements in section
(3) below. Therefore, we accept this alternative and have made the
appropriate change in section (3) below.
Comment: Marathon Petroleum Company, LP commented that the
operating conditions in Table 2 do not reflect what they requested in
their AMEL for the MPGF at their Garyville refinery. They stated that
they needed separate NHVcz limits for the pressure-assisted linear
relief gas oxidizers (LRGO burners) and the steam-assisted steam
kinetic energy combustors (SKEC burners) when both are being used
simultaneously. Marathon explained that the SKEC burners would have a
considerably different NHVcz value because of steam assist. This is
because the steam assist is included in the NHVcz calculation for the
SKEC burners, but not for the LRGO burners, given that the LRGO burners
do not have steam assist.
Response: The EPA acknowledges that the April notice did not
reflect Marathon Petroleum Company, LP's supplemental request for the
Garyville MPGF to maintain separate burner limits such that the SKEC
burners would meet the NHVcz target from the SKEC equation and the LRGO
burners would meet 600 British thermal units per standard cubic feet
(BTU/scf). We discussed with Marathon its supplemental request upon
receiving the comment. As we explained in that discussion, based on our
review of the information provided by Marathon, the steam-to-vent gas
ratio for the SKEC burners is not high enough to significantly affect
the NHVcz during the high pressure flaring scenario. Therefore, we
conclude that the burner requirements as set out in the April 25, 2018,
AMEL document are appropriate. Marathon concurred with this conclusion
in an email response after the comment period closed (available in
Docket ID No. EPA-HQ-OAR-2014-0738 and EPA-HQ-OAR-2010-0682).
Comment: Marathon Petroleum Company, LP commented that the
requirement should be NHVvg = NHVcz with a limit of >=600 BTU/scf for
the LH burner, and NHVcz >=600 BTU/scf for LRGO burners. Marathon notes
that, as explained in its February 2, 2018, and March 27, 2018,
supplemental letters, since the LH burner is air-assisted, therefore,
the LH burner limitations provided in its request correspond to the
NHVvg and not the NHVcz. Marathon further notes that the Petroleum
Refinery requirements at 40 CFR 63.670(m)(1) states that NHVvg = NHVcz
when there is no premix assist air flow.
Response: For the reasons provided in Marathon's comment, we agree
that for the LH burner, which is perimeter air assisted and not pre-mix
air assisted, the NHVvg equals NHVcz. We, therefore, made this change
in Table 2 below.
Comment: ExxonMobil Corporation commented on a typographical
correction in Table 2 for the Baytown, Texas, Flexicoker Flare 26. The
proposed alternative operating condition was listed as >=270 BTU/scf
NHVcz and velocity of <361 feet per second (ft/sec). However, the
performance test results for the Flare 26 demonstrate that the
destruction efficiency met 98 percent at 361 ft/sec.
Response: We accept this correction and made the change in Table 2
to <=361 ft/sec.
Comment: ExxonMobil Corporation commented that the EPA should
include a default molecular weight for pipeline natural gas that
corresponds to an NHV of 920 BTU/scf listed in 40 CFR 63.670(j)(5).
Response: We agree and are specifying the molecular weight of
pipeline natural gas as 16.85 grams per gram mole (g/mol). It would be
burdensome for Exxon to take samples of natural gas to determine
molecular weight, when very little changes in molecular weight are
expected. Therefore, we are specifying the molecular weight of natural
gas of 16.85 can be used. This molecular weight is based on our default
natural gas composition that was used to determine the net heating
value in 40 CFR 63.670.
Comment: ExxonMobil Corporation commented that the accuracy and
calibration requirements in section (1)(f) of the initial Federal
Register document should apply only to flares at chemical plants
seeking AMEL approval since flares such as Exxon's Flare 26 is already
subject to the accuracy and calibration requirements in the Petroleum
Refinery MACT at 40 CFR 63.671(a)(1) and (4) and Table 13.
Response: We agree and have clarified in section (1)(f) below that
the accuracy and calibration requirements listed in Table 4 do not
apply to refinery flares subject to requirements at 40 CFR 63.671(a)(1)
and (4) and Table 13 of 40 CFR part 63, subpart CC.
Comment: ExxonMobil Corporation commented that the Flare 26 follows
the Petroleum Refinery MACT requirement at 40 CFR part 63, subpart CC,
for pilot flame operations and does not use cross-lighting for the
flare operation. They stated that the EPA should clarify in section (2)
that the Flare 26 is only required to maintain flare pilots per the
Petroleum Refinery MACT requirements in 40 CFR 63.670(b).
Response: We agree that the requirements in section (2), which
apply to flares that cross light, should not apply to Flare 26 because
it does not use cross-lighting. We have made this change in section (2)
below.
Comment: ExxonMobil Corporation commented that the EPA should
clarify which reporting requirements apply to the Flare 26 in section
(6) and clarify that the reporting requirements for the flare tip
velocity and NHVcz are applicable when regulated material is routed to
the flare for at least 15 minutes.
Response: While we believe that the records required in section
(6)(c) are essentially the same as the reporting requirements in
Petroleum Refinery NESHAP, 40 CFR part 63, subpart CC, section (6)(c)
requires additional records related to the operation of MPGFs, which do
not apply to Flare 26. Further,
[[Page 46942]]
we agree that the operating limits for NHVcz and Vtip apply whenever
regulated material is routed to the flares for at least 15 minutes, as
specified by 40 CFR part 63, subpart CC; Therefore, we are requiring
that Flare 26 comply with the reporting requirements in the Petroleum
Refinery NESHAP, 40 CFR part 63, subpart CC, instead of section (6) as
part of this AMEL approval. However, MPGFs located at petroleum
refineries must comply with the additional reporting requirements for
MPGFs in (6)(c)(iv) and (v). To avoid other potential confusion, we are
clarifying the applicability of section (6)(c) to all the flares
covered in this notice. Specifically, section (6)(c) below provides
that flares at refineries must meet the requirements in the Petroleum
Refinery MACT in 40 CFR 63.655(g)(11)(i)-(iii), except that the
applicable alternative operating conditions listed in Table 2 apply
instead of the operating limits specified in 40 CFR 63.670(d) through
(f). In addition, for refinery flares that are MPGFs, notification
shall also include records specified in section (6)(c)(iv)-(v). For
LACC MPGFs, the notification shall include the records specified in
section (6)(c)(i)-(v).
III. AMEL for the Flares
Based upon our review of the AMEL requests and the comments
received through the public comment period, we are approving these AMEL
requests and are establishing operating conditions for the flares at
issue. The AMEL and the associated operating conditions are specified
in Table 2 and accompanying paragraphs. These operating conditions will
ensure that these flares will achieve emission reductions at least
equivalent to flares complying with the flare requirements under the
applicable NESHAP and NSPS identified in Table 1.
Table 2--Alternative Operating Conditions
----------------------------------------------------------------------------------------------------------------
Affected
AMEL submitted Company facilities Flare type(s) Alternative operating conditions
----------------------------------------------------------------------------------------------------------------
11/7/17.............. ExxonMobil....... Baytown, TX Elevated gas- >=270 BTU/scf NHV and velocity
Flexicoker Flare assist flare. <=361 (ft/sec).
26.
10/7/17.............. Marathon......... Garyville, LA.... 2 MPGFs.......... When both SKEC and LRGO burners
are being used, the higher of
>=600 BTU/scf NHV or >=127.27
ln(v)-110.87 NHV. When only the
SKEC burner is being used
>=127.27 ln(v)-110.87 NHV.
10/7/17.............. Marathon/ GBR (Texas City, MPGF............. NHV >=600 BTU/scf for the LH
Blanchard TX). burner, and NHV >=600 BTU/scf
Refining. for LRGO burners.
9/19/17.............. Chalmette Chalmette, LA.... Elevated multi- >=1,000 BTU/scf NHV or LFL <=6.5
Refining. point flare. vol%.
5/1/17............... LACC............. Lake Charles, LA. 2 MPGFs.......... >=1075 BTU/scf NHV for INDAIR
Burners; >=800 BTU/scf NHV for
LRGO only.
----------------------------------------------------------------------------------------------------------------
(1) All flares must be operated such that the combustion zone gas
net heating value (NHVcz) or the lower flammability in the combustion
zone (LFLcz) as specified in Table 2 is met. Owners or operators must
demonstrate compliance with the applicable NHVcz or LFLcz specified in
Table 2 on a 15-minute block average. Owners or operators must
calculate and monitor for the NHVcz or LFLcz according to the
following:
(a) Calculation of NHVcz
(i) If an owner or operator elects to use a monitoring system
capable of continuously measuring (i.e., at least once every 15
minutes), calculating, and recording the individual component
concentrations present in the flare vent gas, NHVvg shall be calculated
using the following equation:
[GRAPHIC] [TIFF OMITTED] TN17SE18.002
Where:
NHVvg = Net heating value of flare vent gas, BTU/scf. Flare vent gas
means all gas found just prior to the tip. This gas includes all
flare waste gas (i.e., gas from facility operations that is directed
to a flare for the purpose of disposing the gas), flare sweep gas,
flare purge gas, and flare supplemental gas, but does not include
pilot gas.
i = Individual component in flare vent gas.
n = Number of components in flare vent gas.
xi = Concentration of component i in flare vent gas, volume
fraction.
NHVi = Net heating value of component i determined as the heat of
combustion where the net enthalpy per mole of offgas is based on
combustion at 25 degrees Celsius ([deg]C) and 1 atmosphere (or
constant pressure) with water in the gaseous state from values
published in the literature, and then the values converted to a
volumetric basis using 20 [deg]C for ``standard temperature.'' Table
3 summarizes component properties including net heating values.
(ii) If the owner or operator uses a continuous net heating value
monitor, the owner or operator may, at their discretion, install,
operate, calibrate, and maintain a monitoring system capable of
continuously measuring, calculating, and recording the hydrogen
concentration in the flare vent gas. The owner or operator shall use
the following equation to determine NHVvg for each sample measured via
the net heating value monitoring system.
[GRAPHIC] [TIFF OMITTED] TN17SE18.003
Where:
NHVvg = Net heating value of flare vent gas, BTU/scf.
NHVmeasured = Net heating value of flare vent gas stream as measured
by the continuous net heating value monitoring system, BTU/scf.
xH2 = Concentration of hydrogen in flare vent gas at the time the
sample was input into the net heating value monitoring system,
volume fraction.
938 = Net correction for the measured heating value of hydrogen
(1,212 -274), BTU/scf.
(iii) For non-assisted flare burners, and the GBR LH burner, NHVvg
= NHVcz. For assisted burners, such as the Marathon Garyville MPGF SKEC
burners, and the Exxon Flare 26 gas-assisted burner, NHVcz is
calculated using Equation 3.
[GRAPHIC] [TIFF OMITTED] TN17SE18.004
Where:
NHVcz = Net heating value of combustion
[[Page 46943]]
zone gas, BTU/scf.
NHVvg = Net heating value of flare vent gas for the 15-minute block
period as determined according to (1)(a)(i), BTU/scf.
Qvg = Cumulative volumetric flow of flare vent gas during the 15-
minute block period, scf.
Qag = Cumulative volumetric flow of assist gas during the 15-minute
block period, scf flow rate, scf.
NHVag = Net heating value of assist gas, BTU/scf; this is zero for
air or for steam.
(b) Calculation of LFLcz
(i) The owner or operator shall determine LFLcz from compositional
analysis data by using the following equation:
[GRAPHIC] [TIFF OMITTED] TN17SE18.005
Where:
LFLvg = Lower flammability limit of flare vent gas, volume percent
(vol %).
n = Number of components in the vent gas.
i = Individual component in the vent gas.
[chi]i = Concentration of component i in the vent gas, vol %.
LFLi = Lower flammability limit of component i as determined using
values published by the U.S. Bureau of Mines (Zabetakis, 1965), vol
%. All inerts, including nitrogen, are assumed to have an infinite
LFL (e.g., LFLN2 = [infin], so that [chi]N2/LFLN2 = 0). LFL values
for common flare vent gas components are provided in Table 3.
(ii) For non-assisted flare burners, LFLvg = LFLcz.
(c) Calculation of Vtip
For the ExxonMobil Flare 26, the owner or operator shall calculate
the 15-minute block average Vtip by using the following equation:
[GRAPHIC] [TIFF OMITTED] TN17SE18.006
Where:
Vtip = Flare tip velocity, ft/sec.
Qvg = Cumulative volumetric flow of vent gas over 15-minute block
average period, scf.
Area = Unobstructed area of the flare tip, square ft.
900 = Conversion factor, seconds per 15-minute block average.
(d) For all flare systems specified in this document, the owner or
operator shall install, operate, calibrate, and maintain a monitoring
system capable of continuously measuring the volumetric flow rate of
flare vent gas (Qvg), the volumetric flow rate of total assist steam
(Qs), the volumetric flow rate of total assist air (Qa), and the
volumetric flow rate of total assist gas (Qag).
(i) The flow rate monitoring systems must be able to correct for
the temperature and pressure of the system and output parameters in
standard conditions (i.e., a temperature of 20 [deg]C
(68[emsp14][deg]F) and a pressure of 1 atmosphere).
(ii) Mass flow monitors may be used for determining volumetric flow
rate of flare vent gas provided the molecular weight of the flare vent
gas is determined using compositional analysis so that the mass flow
rate can be converted to volumetric flow at standard conditions using
the following equation:
[GRAPHIC] [TIFF OMITTED] TN17SE18.007
Where:
Qvol = Volumetric flow rate, scf/sec.
Qmass = Mass flow rate, pounds per sec.
385.3 = Conversion factor, scf per pound-mole.
MWt = Molecular weight of the gas at the flow monitoring
location, pounds per pound-mole.
(e) For each measurement produced by the monitoring system used to
comply with (1)(a)(ii), the operator shall determine the 15-minute
block average as the arithmetic average of all measurements made by the
monitoring system within the 15-minute period.
(f) The owner or operator must follow the accuracy and calibration
procedures according to Table 4. Flares at refineries must meet the
accuracy and calibration requirements in the Petroleum Refinery MACT at
40 CFR 63.671(a)(1) and (4) and Table 13. Maintenance periods,
instrument adjustments, or checks to maintain precision and accuracy
and zero and span adjustments may not exceed 5 percent of the time the
flare is receiving regulated material.
Table 3--Individual Component Properties
----------------------------------------------------------------------------------------------------------------
MW (pounds per
Component Molecular formula pound-mole) NHV (BTU/scf) LFL (volume %)
----------------------------------------------------------------------------------------------------------------
Acetylene........................... C2H2...................... 26.04 1,404 2.5
Benzene............................. C6H6...................... 78.11 3,591 1.3
1,2-Butadiene....................... C4H6...................... 54.09 2,794 2.0
1,3-Butadiene....................... C4H6...................... 54.09 2,690 2.0
iso-Butane.......................... C4H10..................... 58.12 2,957 1.8
n-Butane............................ C4H10..................... 58.12 2,968 1.8
cis-Butene.......................... C4H8...................... 56.11 2,830 1.6
iso-Butene.......................... C4H8...................... 56.11 2,928 1.8
trans-Butene........................ C4H8...................... 56.11 2,826 1.7
Carbon Dioxide...................... CO2....................... 44.01 0 [infin]
Carbon Monoxide..................... CO........................ 28.01 316 12.5
Cyclopropane........................ C3H6...................... 42.08 2,185 2.4
Ethane.............................. C2H6...................... 30.07 1,595 3.0
Ethylene............................ C2H4...................... 28.05 1,477 2.7
Hydrogen............................ H2........................ 2.02 * 1,212 4.0
Hydrogen Sulfide.................... H2S....................... 34.08 587 4.0
Methane............................. CH4....................... 16.04 896 5.0
Methyl-Acetylene.................... C3H4...................... 40.06 2,088 1.7
Nitrogen............................ N2........................ 28.01 0 [infin]
Oxygen.............................. O2........................ 32.00 0 [infin]
Pentane+ (C5+)...................... C5H12..................... 72.15 3,655 1.4
Propadiene.......................... C3H4...................... 40.06 2,066 2.16
Propane............................. C3H8...................... 44.10 2,281 2.1
Propylene........................... C3H6...................... 42.08 2,150 2.4
[[Page 46944]]
Water............................... H2O....................... 18.02 0 [infin]
----------------------------------------------------------------------------------------------------------------
* The theoretical net heating value for hydrogen is 274 BTU/scf, but for the purposes of the flare requirement
in this subpart, a net heating value of 1,212 BTU/scf shall be used.
Table 4--Accuracy and Calibration Requirements
----------------------------------------------------------------------------------------------------------------
Parameter Accuracy requirements Calibration requirements
----------------------------------------------------------------------------------------------------------------
Flare Vent Gas Flow Rate.............. 20 percent of flow Performance evaluation biennially (every
rate at velocities ranging 2 years) and following any period of
from 0.1 to 1 foot per second. more than 24 hours throughout which the
5 percent of flow flow rate exceeded the maximum rated
rate at velocities greater flow rate of the sensor, or the data
than 1 foot per second. recorder was off scale. Checks of all
mechanical connections for leakage
monthly. Visual inspections and checks
of system operation every 3 months,
unless the system has a redundant flow
sensor.
Select a representative measurement
location where swirling flow or
abnormal velocity distributions due to
upstream and downstream disturbances at
the point of measurement are minimized.
Flow Rate for All Flows Other Than 5 percent over the Conduct a flow sensor calibration check
Flare Vent Gas. normal range of flow measured at least biennially (every 2 years);
or 1.9 liters per minute (0.5 conduct a calibration check following
gallons per minute), any period of more than 24 hours
whichever is greater, for throughout which the flow rate exceeded
liquid flow. the manufacturer's specified maximum
rated flow rate or install a new flow
sensor.
5 percent over the At least quarterly, inspect all
normal range of flow measured components for leakage, unless the
or 280 liters per minute (10 continuous parameter monitoring system
cubic feet per minute), (CPMS) has a redundant flow sensor.
whichever is greater, for gas
flow.
5 percent over the Record the results of each calibration
normal range measured for check and inspection.
mass flow. Locate the flow sensor(s) and other
necessary equipment (such as
straightening vanes) in a position that
provides representative flow; reduce
swirling flow or abnormal velocity
distributions due to upstream and
downstream disturbances.
Pressure.............................. 5 percent over the Review pressure sensor readings at least
normal range measured or 0.12 once a week for straight-line
kilopascals (0.5 inches of (unchanging) pressure and perform
water column), whichever is corrective action to ensure proper
greater. pressure sensor operation if blockage
is indicated.
Performance evaluation annually and
following any period of more than 24
hours throughout which the pressure
exceeded the maximum rated pressure of
the sensor, or the data recorder was
off scale. Checks of all mechanical
connections for leakage monthly. Visual
inspection of all components for
integrity, oxidation, and galvanic
corrosion every 3 months, unless the
system has a redundant pressure sensor.
Select a representative measurement
location that minimizes or eliminates
pulsating pressure, vibration, and
internal and external corrosion.
Net Heating Value by Calorimeter...... 2 percent of span. Calibration requirements--follow
manufacturer's recommendations at a
minimum.
Temperature control (heated and/or
cooled as necessary) the sampling
system to ensure proper year-round
operation.
Where feasible, select a sampling
location at least 2 equivalent
diameters downstream from and 0.5
equivalent diameters upstream from the
nearest disturbance. Select the
sampling location at least 2 equivalent
duct diameters from the nearest control
device, point of pollutant generation,
air in-leakages, or other point at
which a change in the pollutant
concentration or emission rate occurs.
Net Heating Value by Gas Chromatograph As specified in Performance Follow the procedure in PS 9 of 40 CFR
Standard (PS) 9 of 40 CFR part 60, appendix B, except that a
part 60, appendix B. single daily mid-level calibration
check can be used (rather than
triplicate analysis), the multi-point
calibration can be conducted quarterly
(rather than monthly), and the sampling
line temperature must be maintained at
a minimum temperature of 60 [deg]C
(rather than 120 [deg]C).
Hydrogen Analyzer..................... 2 percent over the Specify calibration requirements in your
concentration measured, or site specific CPMS monitoring plan.
0.1 volume, percent, Calibration requirements--follow
whichever is greater. manufacturer's recommendations at a
minimum.
Specify the sampling location at least 2
equivalent duct diameters from the
nearest control device, point of
pollutant generation, air in-leakages,
or other point at which a change in the
pollutant concentration occurs.
----------------------------------------------------------------------------------------------------------------
(2) The flare system shall be operated with a flame present at all
times when in use. Additionally, each stage that cross-lights must have
at least two pilots with a continuously lit pilot flame, except for
Chalmette's No. 1 Flare, which has one pilot for each stage, excluding
stages 8A and 8B. Each pilot flame must be continuously monitored by a
thermocouple or any other equivalent device used to detect the presence
of a flame. The time, date, and duration of any complete loss of pilot
flame on any of the burners must be recorded. Each monitoring device
must be maintained or replaced at a frequency in accordance with the
manufacturer's specifications. The ExxonMobil flare, Flare 26, and
GBR's LH flare must meet the requirements in the Petroleum Refinery
MACT at 40 CFR 63.670(b) instead of the requirements herein in section
(2).
(3) Flares at refineries shall comply with the Petroleum Refinery
MACT requirements of 40 CFR 63.670(h). For LACC, LLC's MPGFs, the flare
system shall be operated with no visible emissions except for periods
not to exceed a total of 5 minutes during any
[[Page 46945]]
2 consecutive hours. A video camera that is capable of continuously
recording (i.e., at least one frame every 15 seconds with time and date
stamps) images of the flare flame and a reasonable distance above the
flare flame at an angle suitable for visible emissions observations
must be used to demonstrate compliance with this requirement. For
LACC's enclosed ground flare, LACC must install a video camera that is
capable of continuously recording (i.e., at least one frame every 15
seconds with time and date stamps) the stack exhaust exit at a
reasonable distance and at an angle suitable for visible emissions
observation in order to demonstrate compliance with this requirement.
The owner or operator must provide real-time video surveillance camera
output to the control room or other continuously manned location where
the video camera images may be viewed at any time.
(4) For the MPGFs and Chalmette's No. 1 Flare, the owner or
operator of a flare system shall install and operate pressure
monitor(s) on the main flare header, as well as a valve position
indicator monitoring system capable of monitoring and recording the
position for each staging valve to ensure that the flare operates
within the range of tested conditions or within the range of the
manufacturer's specifications. Flares at refineries must meet the
accuracy and calibration requirements in the Petroleum Refinery MACT at
40 CFR 63.671(a)(1) and (4) and Table 13. The pressure monitor at LACC
shall meet the accuracy and calibration requirements in Table 4.
Maintenance periods, instrument adjustments or checks to maintain
precision and accuracy, and zero and span adjustments may not exceed 5
percent of the time the flare is receiving regulated material.
(5) Recordkeeping Requirements
(a) All data must be recorded and maintained for a minimum of 3
years or for as long as required under applicable rule subpart(s),
whichever is longer.
(6) Reporting Requirements
(a) The information specified in section III(6)(b) and (c) below
must be reported in the timeline specified by the applicable rule
subpart(s) for which the flare will control emissions.
(b) Owners or operators shall include the final AMEL operating
requirements for each flare in their initial Notification of Compliance
status report.
(c) The owner or operator shall notify the Administrator of periods
of excess emissions in their Periodic Reports. The owner or operator of
refinery flares shall meet the reporting requirements in the Petroleum
Refinery MACT in 40 CFR 63.655(g)(11)(i)-(iii), except that the
applicable alternative operating conditions listed in Table 2 apply
instead of the operating limits specified in 40 CFR 63.670(d) through
(f). In addition, for refinery flares that are MPGFs, notification
shall also include records specified in section (iv)-(v) below. For
LACC MPGFs, the notification shall include the records specified in
section (i)-(v) below.
(i) Records of each 15-minute block for all flares during which
there was at least 1 minute when regulated material was routed to the
flare and a complete loss of pilot flame on a stage of burners
occurred, and for all flares, records of each 15-minute block during
which there was at least 1 minute when regulated material was routed to
the flare and a complete loss of pilot flame on an individual burner
occurred.
(ii) Records of visible emissions events (including the time and
date stamp) that exceed more than 5 minutes in any 2-hour consecutive
period.
(iii) Records of each 15-minute block period for which an
applicable combustion zone operating condition (i.e., NHVcz or LFLcz)
is not met for the flare when regulated material is being combusted in
the flare. Indicate the date and time for each period, the NHVcz and/or
LFLcz operating parameter for the period, the type of monitoring system
used to determine compliance with the operating parameters (e.g., gas
chromatograph or calorimeter), and also indicate which high-pressure
stages were in use.
(iv) Records of when the pressure monitor(s) on the main flare
header show the flare burners are operating outside the range of tested
conditions or outside the range of the manufacturer's specifications.
Indicate the date and time for each period, the pressure measurement,
the stage(s) and number of flare burners affected, and the range of
tested conditions or manufacturer's specifications.
(v) Records of when the staging valve position indicator monitoring
system indicates a stage of the flare should not be in operation and is
or when a stage of the flare should be in operation and is not.
Indicate the date and time for each period, whether the stage was
supposed to be open, but was closed, or vice versa, and the stage(s)
and number of flare burners affected.
Dated: September 11, 2018.
Panagiotis Tsirigotis,
Director, Office of Air Quality Planning and Standards.
[FR Doc. 2018-20148 Filed 9-14-18; 8:45 am]
BILLING CODE 6560-50-P