Applicability Determination Index (ADI) Database System Recent Posting: Applicability Determinations, Alternative Monitoring Decisions, and Regulatory Interpretations Pertaining to Standards of Performance for New Stationary Sources, National Emission Standards for Hazardous Air Pollutants, and the Stratospheric Ozone Protection Program, 22176-22186 [2015-09242]
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22176
Federal Register / Vol. 80, No. 76 / Tuesday, April 21, 2015 / Notices
time on the specified comment date.
Protests may be considered, but
intervention is necessary to become a
party to the proceeding.
eFiling is encouraged. More detailed
information relating to filing
requirements, interventions, protests,
service, and qualifying facilities filings
can be found at: https://www.ferc.gov/
docs-filing/efiling/filing-req.pdf. For
other information, call (866) 208–3676
(toll free). For TTY, call (202) 502–8659.
Dated: April 15, 2015.
Nathaniel J. Davis, Sr.,
Deputy Secretary.
[FR Doc. 2015–09178 Filed 4–20–15; 8:45 am]
BILLING CODE 6717–01–P
DEPARTMENT OF ENERGY
Federal Energy Regulatory
Commission
Persons unable to file electronically
should submit an original and 5 copies
of the intervention or protest to the
Federal Energy Regulatory Commission,
888 First Street NE., Washington, DC
20426.
The filings in the above-referenced
proceeding(s) are accessible in the
Commission’s eLibrary system by
clicking on the appropriate link in the
above list. They are also available for
review in the Commission’s Public
Reference Room in Washington, DC.
There is an eSubscription link on the
Web site 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.
Dated: April 14, 2015.
Nathaniel J. Davis, Sr.,
Deputy Secretary.
[Docket No. ER15–1463–000]
tkelley on DSK3SPTVN1PROD with NOTICES
Triton Energy, Inc.; Supplemental
Notice That Initial Market-Based Rate
Filing Includes Request for Blanket
Section 204 Authorization
[FR Doc. 2015–09044 Filed 4–20–15; 8:45 am]
This is a supplemental notice in the
above-referenced proceeding, of Triton
Energy, Inc.’s application for marketbased rate authority, with an
accompanying rate schedule, noting that
such application includes a request for
blanket authorization, under 18 CFR
part 34, of future issuances of securities
and assumptions of liability.
Any person desiring to intervene or to
protest should file with the Federal
Energy Regulatory Commission, 888
First Street NE., Washington, DC 20426,
in accordance with Rules 211 and 214
of the Commission’s Rules of Practice
and Procedure (18 CFR 385.211 and
385.214). Anyone filing a motion to
intervene or protest must serve a copy
of that document on the Applicant.
Notice is hereby given that the
deadline for filing protests with regard
to the applicant’s request for blanket
authorization, under 18 CFR part 34, of
future issuances of securities and
assumptions of liability is May 4, 2015.
The Commission encourages
electronic submission of protests and
interventions in lieu of paper, using the
FERC Online links at https://
www.ferc.gov. To facilitate electronic
service, persons with Internet access
who will eFile a document and/or be
listed as a contact for an intervenor
must create and validate an
eRegistration account using the
eRegistration link. Select the eFiling
link to log on and submit the
intervention or protests.
ENVIRONMENTAL PROTECTION
AGENCY
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BILLING CODE 6717–01–P
[FRL–9926–65–OECA]
Applicability Determination Index (ADI)
Database System Recent Posting:
Applicability Determinations,
Alternative Monitoring Decisions, and
Regulatory Interpretations Pertaining
to Standards of Performance for New
Stationary Sources, National Emission
Standards for Hazardous Air
Pollutants, and the Stratospheric
Ozone Protection Program
Environmental Protection
Agency (EPA).
ACTION: Notice of availability.
AGENCY:
This notice announces
applicability determinations, alternative
monitoring decisions, and regulatory
interpretations that EPA has made
under the New Source Performance
Standards (NSPS); the National
Emission Standards for Hazardous Air
Pollutants (NESHAP); and/or the
Stratospheric Ozone Protection
Program.
SUMMARY:
An
electronic copy of each complete
document posted on the Applicability
Determination Index (ADI) database
system is available on the Internet
through the Resources and Guidance
Documents for Compliance Assistance
page of the Clean Air Act Compliance
Monitoring Web site under ‘‘Air’’ at:
FOR FURTHER INFORMATION CONTACT:
PO 00000
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https://www2.epa.gov/compliance/
resources-and-guidance-documentscompliance-assistance. The letters and
memoranda on the ADI may be located
by control number, date, author,
subpart, or subject search. For questions
about the ADI or this notice, contact
Maria Malave at EPA by phone at: (202)
564–7027, or by email at:
malave.maria@epa.gov. For technical
questions about individual applicability
determinations or monitoring decisions,
refer to the contact person identified in
the individual documents, or in the
absence of a contact person, refer to the
author of the document.
SUPPLEMENTARY INFORMATION:
Background
The General Provisions of the NSPS
in 40 Code of Federal Regulations (CFR)
part 60 and the General Provisions of
the NESHAP in 40 CFR part 61 provide
that a source owner or operator may
request a determination of whether
certain intended actions constitute the
commencement of construction,
reconstruction, or modification. EPA’s
written responses to these inquiries are
commonly referred to as applicability
determinations. See 40 CFR 60.5 and
61.06. Although the part 63 NESHAP
regulations [which include Maximum
Achievable Control Technology (MACT)
and/or Generally Available Control
Technology (GACT)standards] and
§ 111(d) of the Clean Air Act (CAA)
contain no specific regulatory provision
providing that sources may request
applicability determinations, EPA also
responds to written inquiries regarding
applicability for the part 63 and § 111(d)
programs. The NSPS and NESHAP also
allow sources to seek permission to use
monitoring or recordkeeping that is
different from the promulgated
requirements. See 40 CFR 60.13(i),
61.14(g), 63.8(b)(1), 63.8(f), and 63.10(f).
EPA’s written responses to these
inquiries are commonly referred to as
alternative monitoring decisions.
Furthermore, EPA responds to written
inquiries about the broad range of NSPS
and NESHAP regulatory requirements as
they pertain to a whole source category.
These inquiries may pertain, for
example, to the type of sources to which
the regulation applies, or to the testing,
monitoring, recordkeeping, or reporting
requirements contained in the
regulation. EPA’s written responses to
these inquiries are commonly referred to
as regulatory interpretations.
EPA currently compiles EPA-issued
NSPS and NESHAP applicability
determinations, alternative monitoring
decisions, and regulatory
interpretations, and posts them to the
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ADI. In addition, the ADI contains EPAissued responses to requests pursuant to
the stratospheric ozone regulations,
contained in 40 CFR part 82. The ADI
is an electronic index on the Internet
with over one thousand EPA letters and
memoranda pertaining to the
applicability, monitoring,
recordkeeping, and reporting
requirements of the NSPS, NESHAP,
and stratospheric ozone regulations.
Users can search for letters and
memoranda by date, office of issuance,
subpart, citation, control number, or by
string word searches.
Today’s notice comprises a summary
of 56 such documents added to the ADI
on April 7, 2015. This notice lists the
subject and header of each letter and
memorandum, as well as a brief abstract
of the letter or memorandum. Complete
copies of these documents may be
obtained from the ADI through the
OECA Web site at: www.epa.gov/
compliance/monitoring/programs/caa/
adi.html.
Summary of Headers and Abstracts
The following table identifies the
database control number for each
document posted on the ADI database
system on April 7, 2015; the applicable
category; the section(s) and/or subpart(s)
of 40 CFR part 60, 61, or 63 (as
applicable) addressed in the document;
and the title of the document, which
provides a brief description of the
subject matter.
22177
We have also included an abstract of
each document identified with its
control number after the table. These
abstracts are provided solely to alert the
public to possible items of interest and
are not intended as substitutes for the
full text of the documents. This notice
does not change the status of any
document with respect to whether it is
‘‘of nationwide scope or effect’’ for
purposes of CAA § 307(b)(1). For
example, this notice does not convert an
applicability determination for a
particular source into a nationwide rule.
Neither does it purport to make a
previously non-binding document
binding.
ADI DETERMINATIONS UPLOADED ON APRIL 7, 2015
Control Number
Categories
Subparts
Title
M110015 ................
MACT, PART 63
NESHAP, NSPS.
NSPS ....................
CC, G, Kb .............
Rule Interpretation on Raw Data Definition and Retention for Storage Vessels.
OOO ......................
Applicability of Rule to Gypsum Handling Equipment at a Power Plant with
Fuel Gas Desulfurization Units.
Alternative Monitoring Plan for Low Sulfur Bearing Fuel Gas Stream.
Performance Test Waiver Request for EAF Secondary Dust Collection System.
Alternative Monitoring Plan For Grab Sampling in Lieu of Continuous Monitoring of Caustic Scrubbers.
Applicability Determination for NESHAP Subparts J and V Benzene Fugitive
Equipment Leaks.
Alternate Work Practice—SRU Sulfur Pit Bypass Lines.
1400038 .................
1100018 .................
Z140006 .................
M120012 ................
Z120001 .................
M120015 ................
Z140005 .................
M120018 ................
NSPS ....................
MACT, Part 63
NESHAP.
MACT, PART 63
NESHAP.
Part 61 NESHAP ..
MACT, PART 63
NESHAP, NSPS.
Part 63 NESHAP ..
J ............................
YYYYY ..................
FFFF .....................
J, V ........................
J, UUU ..................
WWWWWW ..........
J, UUU ..................
Applicability Determination for Research and Development Unit under
NESHAP Subpart WWWWWW.
Alternative Monitoring in Lieu of COMS for Regenerators.
NNNNN .................
Alternative Monitoring for Caustic Scrubber Parametric Monitoring.
D ............................
G, H .......................
Stack COMS Relocation Determined By Equivalency Testing.
Approval of a Common Report Schedule—MACT Subparts G and H.
J
J
J
J
Alternative Monitoring for Hydrocracker Feed Surge Drum Vent Stream.
Alternative Monitoring for NHT Feed Surge Drum Off—Gas Vent Stream.
Alternative Hydrogen Sulfide Monitoring for Oleflex Reactor Vent Stream.
Alternative Hydrogen Sulfide Monitoring for Truck Loading, Storage Tank and
Well Vent Gas Streams.
Single-Point Testing In Place of Method 1 or 1A—Engine Emission Testing.
Applicability of NSPS Subparts Kb and KKK for a Vapor Recovery Unit and
Storage Tanks.
Timing Issues in Determining MACT and Title V Applicability.
.................
.................
.................
.................
MACT, PART 63
NESHAP, NSPS.
MACT, PART 63
NESHAP.
NSPS ....................
MACT, PART 63
NESHAP.
NSPS ....................
NSPS ....................
NSPS ....................
NSPS ....................
1200046 .................
1200062 .................
NSPS ....................
NSPS ....................
JJJJ .......................
KKK, Kb ................
M120027 ................
MACT, PART 63
NESHAP.
MACT, PART 63
NESHAP.
NSPS ....................
JJJ .........................
M120020 ................
1200038 .................
M120021 ................
1200039
1200040
1200041
1200042
M120029 ................
1200087 .................
Z140004 .................
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1400016 .................
1400019 .................
A140003 ................
M140006 ................
M140008 ................
1400021 .................
M140009 ................
M140010 ................
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MACT, PART 63
NESHAP.
NSPS ....................
NSPS ....................
Asbestos ...............
MACT, PART 63
NESHAP.
MACT, PART 63
NESHAP.
NSPS ....................
MACT, PART 63
NESHAP.
MACT, PART 63
NESHAP.
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............................
............................
............................
............................
S ............................
CC, G ....................
Approval of an Alternative Monitoring Frequency under the Pulp and Paper
MACT.
Revision to NSPS Method of Determining Compliance for Combined Effluent
NOX CEMS.
Exemption for Emergency Engines at Commercial Area Sources from RICE
NESHAP—Regulatory Interpretation.
Applicability Determination for Commercially Operated Contraband Incinerator.
Guidance on Alternative Compliance Timeline Requests for Landfill.
Applicability of the Asbestos NESHAP as it Applies to Concrete Bridges.
Continuing Requirements when Surface Coating Operations no Longer Meets
Affected Source Criteria.
Interpretation of Required Tank Inspection Frequency.
Dc, Ja ....................
ZZZZ .....................
NOx Requirements for Boilers.
Disapproval of an Engine De-Rate Proposal.
ZZZZ .....................
Approval of an Engine De-rate Proposal.
Db ..........................
ZZZZ .....................
EEEE, FFFF ..........
WWW ....................
M ...........................
A, MMMM ..............
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Federal Register / Vol. 80, No. 76 / Tuesday, April 21, 2015 / Notices
ADI DETERMINATIONS UPLOADED ON APRIL 7, 2015—Continued
Control Number
Categories
Subparts
Title
M140011 ................
IIII, ZZZZ ...............
M140012 ................
M140013 ................
M140014 ................
Z140007 .................
MACT, PART 63
NESHAP, NSPS.
PART 63 NESHAP
PART 63 NESHAP
PART 63 NESHAP
Part 63 NESHAP ..
A140004 ................
A140005 ................
Asbestos ...............
Asbestos ...............
M140016 ................
1400022 .................
MACT, PART 63
NESHAP.
NSPS ....................
J ............................
1400023 .................
NSPS ....................
J ............................
1400024 .................
NSPS ....................
J ............................
1400025 .................
1400026 .................
1400027 .................
KKK .......................
OOOO ...................
J, UUU ..................
1400028 .................
NSPS ....................
NSPS ....................
MACT, PART 63
NESHAP, NSPS.
NSPS ....................
1400029 .................
1400030 .................
1400031 .................
NSPS ....................
NSPS ....................
NSPS ....................
Ja ..........................
Ja ..........................
J, Ja ......................
1400032 .................
NSPS ....................
OOOO ...................
1400033 .................
NSPS ....................
J, Ja ......................
1400034 .................
NSPS ....................
A, D .......................
1400035 .................
NSPS ....................
Ec ..........................
1400036 .................
1400037 .................
NSPS ....................
NSPS ....................
Db ..........................
J ............................
1100017 .................
NSPS ....................
J ............................
Applicability to a Non-stationary Engine Relocated For Use as a Stationary
Engine.
Determination of Force Majeure.
Regulatory Interpretation of Tune-up Requirements for Spreader Stoker Boiler.
Compliance Extension for Replacement Energy Source.
Rule Applicability to HAP-Containing Mixing Operations to Produce AcrylicBased Stucco.
Small Residence Exemption.
Interim Method of Determination of Asbestos in Bulk Insulation Samples and
Transmission Electron Microscopy.
Categorization and applicability of a Boiler using natural gas and tire derived
fuel.
NSPS Fuel Gas Definition and Alternative Monitoring of Marine Vessel Loading Vapors.
Conditional CEMS Exemption Approval for Low Sulfur Combustion of Off-gas
Vent Stream.
CEMS Exemption in Lieu of Alternative Monitoring for Combustion of Commercial Grade Natural Gas and Refinery Fuel Gas.
Regulatory Interpretation for Gas Plant Propane Refrigeration System.
Applicability Determination for Reciprocating Compressors.
Alternative Monitoring Plan for Wet Gas Scrubber on a Fluidized Catalytic
Cracking Unit.
Alternative Monitoring and Waiver of Testing Request for Distillation Vent Gas
to Process Heaters.
Request for Alternative Monitoring of Condensate Splitter Flare.
Alternative Monitoring Plan for Oxygen in Boiler Stack Emissions.
Alternative Hydrogen Sulfide Monitoring in Tank Degassing Vapors Combusted in Portable Thermal Oxidizers.
Regulatory Interpretation—Submission of Photographs For Natural Gas Well
Completion Annual Reports.
Alternative Hydrogen Sulfide Monitoring in Tank Degassing Vapors Combusted in Portable Thermal Oxidizers.
Regulatory Interpretation—Demonstrating Continuous Compliance and Reporting Excess Emissions for NSPS and Title V.
Alternative Operating Parameters for a Wet Gas Scrubber Followed By Carbon Adsorber and Cartridge Filter at an HMIWI.
Alternative Monitoring Plan for Fuel Analysis from Subpart Db Boiler.
Conditional CEMS Exemption Approval for Low Sulfur Combustion of Off-gas
Vent Stream.
Alternative Monitoring of Opacity for a Wet Gas Scrubber.
A, JJJJJJ ...............
JJJJJJ ...................
JJJJJJ ...................
BBBBBBB,
VVVVVV.
M ...........................
M ...........................
DDDDD .................
NNN, RRR ............
Abstracts
tkelley on DSK3SPTVN1PROD with NOTICES
Abstract for [M110015]
Q1: What is EPA interpretation of raw
data, in reference to 40 CFR 63.654 and
40 CFR 60.115b and the storage vessel
recordkeeping provisions in NSPS
subpart Kb, and Part 63 NESHAP
subparts G and CC?
A1: EPA indicated to the Texas
Commission on Environmental Quality
Region 14 that although the phrase ‘‘raw
data’’ does not have a regulatory
definition, EPA has issued guidance on
this subject to deal with air pollution
measurement systems and the quality
assurance procedures associated with
such systems. In general, raw data is
data that is captured and recorded on
field data sheets during a measurement
of some sort, such as sampling of
emissions or testing of control
equipment.
Q2: May a source, after transferring
data from field data sheets into an
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electronic database, dispose of the field
data sheets?
A2: No. Original field data sheets
must be preserved whenever any sort of
emissions sampling or equipment
testing, such as measuring seal gaps in
a storage tank, is performed.
Transferring raw data into a database
can introduce additional error in data
transcription and entry.
Abstract for [1400038]
Q1: Is gypsum handling equipment at
the Dominion Chesterfield Power
Station in Chester, Virginia, subject to
NSPS subpart OOO for Nonmetallic
Mineral Processing Plants? Dominion
acknowledges that a limestone crushing
process at Chesterfield is subject to
subpart OOO.
A1: Yes. The gypsum handling
equipment is also subject to NSPS
subpart OOO. The facility meets the
definition of a nonmetallic mineral
processing plant, and each affected
facility at Chesterfield is subject to
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subpart OOO, including the belt
conveyors used to transfer gypsum to
storage sheds or loading docks.
Q2: Must the crushing or grinding of
gypsum take place in the ‘‘production
line’’ to be subject to subpart OOO?
A2: No. The definition of production
line does not require that every affected
facility be part of a production line with
crushing or grinding. If crushing or
grinding of a nonmetallic mineral
occurs anywhere at the facility, then
each affected facility is subject
regardless of its location within the
plant.
Q3: Are there other power plants with
flue gas desulfurization units where the
gypsum handling equipment is subject
to subpart OOO?
A3: Yes. Based on a brief review of
similar permits, EPA found at least three
such power plants with permits where
subpart OOO was applied to the gypsum
handling equipment.
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Abstract for [1100018]
Q: Does EPA approve the
ConocoPhillips Sweeny, Texas Refinery
Alternate Monitoring Plan (AMP) under
NSPS subpart J? Conoco claims an
exemption per 40 CFR 60.105(a)(4)(iv)
because Flare #7 receives fuel gas waste
from catalytic reforming units.
A: Yes. EPA conditionally approves
ConocoPhillips’s AMP. Conditional
approval of alternative monitoring
parameters is granted based on a
requirement that the flare receive low
sulfur/sulfide bearing streams waste fuel
gas only from catalytic reformers. Any
significant increase in the sulfur/sulfide
concentration detected in the stream
would initiate continuous monitoring
under 40 CFR 60.105(a)(3) or (4).
Introduction of other streams that are
not from catalytic reformers require
application of another AMP.
Abstract for [Z140006]
Q1: Does EPA approve of a waiver in
the number of performance test
sampling locations required to comply
with particulate stack sampling
requirements under 40 CFR part 63
subpart YYYYY for the electric arc
furnace at ArcelorMittal’s LaPlace,
Louisiana facility?
A1: No. Based on the information
provided, EPA could not approve the
request to sample only three of the six
emission points. Without the results of
a previous performance test which
included results for all six emission
points, EPA could not confirm that
emissions from three of the emission
points might be representative of all six.
Additionally, EPA reserves the right to
determine which emission points
should be sampled.
Q2: Can the 60-day testing
notification requirement be waived,
allowing ArcelorMittal a 30-day
notification period?
A2: Yes. Based on the timing of
ArcelorMittal’s testing waiver request
and the testing schedule, EPA is
allowing a reduced testing notification
timeframe. EPA asked that ArcelorMittal
provide the Louisiana Department of
Environmental Quality (DEQ) a written
notice at least ten (10) days prior to the
intended testing dates in order that DEQ
be afforded the opportunity to observe
the testing.
tkelley on DSK3SPTVN1PROD with NOTICES
Abstract for [M120012]
Q: Does EPA approve the Alternative
Monitoring Plan (AMP) for monitoring
the caustic strength of scrubber effluent
by a grab sample monitoring system, in
lieu of continuously measuring caustic
strength, under MACT subpart FFFF for
the miscellaneous organic chemical
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Jkt 235001
manufacturing process units and caustic
scrubbers controlling Group 1 Process
Vents at the Dow Chemical plant in La
Porte, Texas?
A: Yes. EPA approves the AMP based
on the information provided. The plan
to monitor scrubber caustic strength by
grab sampling, in lieu of continuously
measuring caustic strength, is
technically acceptable. Subpart FFFF
requires that the scrubbers be monitored
continuously either via continuous pH
measurement and recording as specified
in 40 CFR 63.994(c)(1)(i) and
63.998(a)(2)(ii)(D), or via continuously
monitoring and recording the caustic
strength of the effluent. Use of a
continuous pH meter or caustic strength
analyzer may be unreliable due to
fouling. The AMP includes frequent
grab sampling to monitor caustic
strength based on a worst case loading
scenario.
Abstract for [Z120001]
Q: Is an inter-plant pipeline which
transports liquids that are at least 10
percent benzene by weight between two
major source facilities, each belonging
to Equistar Chemicals in Alvin, Texas,
subject to part 61 NESHAP subparts J
and V?
A: Yes. An inter-plant pipeline that
transports benzene liquids is an
emission source that is in benzene
service according to 40 CFR 61.110 and
61.111, regardless of whether or not the
pipeline is defined as a discrete process
unit. 40 CFR 61.110(a) includes valves,
connectors or systems in benzene
service, regardless of their location, and
subpart V applies as the leak detection
provision for subpart J, per 40 CFR
61.111.
Abstract for [M120015]
Q: Does EPA approve an alternate
work practice for monitoring hydrogen
sulfide (H2S) at bypass lines associated
with sulfur recovery unit (SRU) sulfur
pits, which are subject to both MACT
subpart UUU and NSPS subpart J, and
the terms of a Consent Decree (CD), at
the Flint Hills Resources Corpus Christi,
Texas East and West refineries?
A: No. EPA does not approve the
alternate work practice because it would
be in direct conflict with both the rule
and the intent of the CD, and would
result in non-compliance. The SRUs and
sulfur pits are subject to a CD that
requires sulfur pit emissions to be
continuously monitored and counted
toward SRU total emissions for
compliance demonstration with the
NSPS subpart J limit for sulfur dioxide
(SO2). Since the alternative work
practice proposed by Flint Hills did not
include continuous monitoring per 40
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22179
CFR 60.104(a)(2), the data necessary to
comply with the portion of the CD
requiring aggregation of sulfur pit
emissions for compliance demonstration
with the NSPS subpart J SO2 limit
would not be collected.
Abstract for [Z140005]
Q: Does EPA approve an exemption
from NESHAP subpart WWWWWW
under the definition of research and
development for the electroplating and
surface finishing facility at Los Alamos
National Laboratory in New Mexico?
A: Yes. Based on a review of 40 CFR
63.11505(d)(2) and the definition of a
research and development process unit
at 40 CFR 63.11511, EPA determines
that the facility meets the definition and
is not subject to NESHAP subpart
WWWWWW.
Abstract for [M120018]
Q: Will EPA approve Motiva
Enterprises’ (Motiva) Alternative
Monitoring Plan (AMP) under 40 CFR
60.8 and 60.13(i)(3) for monitoring wet
gas scrubbers (WGS) on a refinery Fluid
Catalytic Cracking Unit (FCCU), in lieu
of a Continuous Opacity Monitoring
System (COMS), due to moisture
interference on opacity readings in the
stack, to demonstrate compliance with
the opacity limit under 40 CFR
60.102(a)(2) and requirements of MACT
subpart UUU at Motiva’s Port Arthur,
Texas refinery?
A: Yes. EPA conditionally approves
Motiva’s AMP. A performance test is
necessary to establish Operating
Parameter Limits (OPLs) and other
operating and monitoring conditions
required for demonstrating compliance
with NSPS subpart J, MACT subpart
UUU and the Consent Decree for each
WGS. The EPA response letter specifies
the operating conditions, operating
parameters, test notice deadlines, and
notification content that are conditions
of the approval. Interim OPLs are
provided.
Abstract for [M120020]
Q: Does EPA approve the Alternative
Monitoring Plan (AMP) for parametric
monitoring on caustic scrubbers used to
control hydrochloric acid emissions
from storage tanks, loading, and process
vents under 40 CFR part 63 subpart
NNNNN at the Rubicon facility in
Geismar, Louisiana?
A: Yes. Based on the information
provided in Rubicon’s request, EPA
conditionally approves the AMP. A
minimum pH operating parameter limit
(OPL), and a minimum recirculating
liquid flow rate, pursuant to 40 CFR
63.9020(e)(1)(i), must be established
during a performance test conducted
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under worst case emissions operating
scenario. The scrubbers’ effectiveness in
meeting subpart NNNNN emission
standards during normal operations will
be ensured by continuous monitoring of
the two OPLs.
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Abstract for [1200038]
Q1: Can equivalency testing be
approved to relocate the flue gas
continuous opacity monitoring system
(COMS) on the stack outlet of a wet gas
scrubber (WGS) covered under NSPS
subpart D at the Texas Municipal Power
Agency (TMPA) Gibbons Creek Electric
Steam Generating Station Unit 1?
A1: Yes. 40 CFR part 60 Appendix B
Performance Specification 1 (PS 1)
Section 8.1 (2)(i) and (ii) specify
measurement location and light beam
path requirements for COMS. If the
proposed alternate COMS locations do
not meet these requirements,
equivalency testing must be conducted
in accordance with PS 1 Section 8.1
(2)(iii) for each possible alternative
location. Based on the test proposal,
EPA approves the request for
conducting preliminary equivalency
testing only, with a 60-day notification
provided to the State authority.
Q2: What if there are separate ducts
that split the vent stream gas flow?
A2: Relocation and the preliminary
equivalency testing must include the
use of two COMS units in order to
provide opacity readings representative
of total emissions.
Q3: What must the facility do to
obtain subsequent approval for
permanent relocation of the stack
COMS?
A3: TMPA must provide the data and
operating information from the
preliminary equivalency testing for the
alternative location ultimately selected,
in accordance with the applicable
performance test reporting requirements
of NSPS subparts A and D. In
accordance with PS 1 Section 8.1
(2)(iii), the average opacity value
measured at each temporary COMS at
the selected alternate location must be
within +/¥ 10 percent of the average
opacity value measured at the existing
flue gas stack COMS, and the difference
between any two average opacity values
must be less than 2 percent opacity
(absolute value).
Abstract for [M120021]
Q: Does EPA approve a common
schedule for submitting periodic reports
under the Hazardous Organic part 63
NESHAP, subparts G and H, at the
Union Carbide Texas City, Texas
facility?
A: Yes. EPA approves the common
schedule provided the reporting
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requirement of 40 CFR 63.152(c)(1) is
satisfied, which only allows a 60-day lag
between the end of the reporting period
and the due date of a periodic report.
EPA reviewed the requirements of 40
CFR 63.10(a)(6) and 63.9(i), and
concurred that the proposed reporting
schedule satisfies the requirements of 40
CFR 63.152(c)(1).
Abstract for [1200039]
Q: Does EPA approve an Alternative
Monitoring Plan (AMP) for monitoring
hydrogen sulfide (H2S) for a refinery
hydrocracker feed surge drum off-gas
vent stream combusted at four
hydrocracker heaters at the Valero
Refining Corpus Christi, Texas West
refinery?
A: Yes. EPA approves Valero’s AMP
based on the description of the process
vent streams, the design of the vent gas
controls, and the H2S monitoring data
furnished. The approval specifies
operating parameter limits for total
sulfur and temperature. Valero must
follow the seven step process detailed in
the Valero consent decree appendix on
Alternative Monitoring Plans for NSPS
subpart J Refinery Fuel Gas.
Abstract for [1200040]
Q: Does EPA approve an Alternative
Monitoring Plan (AMP) for monitoring
hydrogen sulfide (H2S) for a refinery
process feed surge drum off-gas vent
stream combusted at a charge heater
under NSPS subpart J at the Valero
Refining Corpus Christi, Texas West
refinery?
A: Yes. EPA approves Valero’s AMP
based on the description of the process
vent stream, the design of the vent gas
controls, and the H2S monitoring data
furnished. The approval specifies
operating parameter limits for total
sulfur and temperature. Valero must
follow the seven step process detailed in
the Valero consent decree appendix on
Alternative Monitoring Plans for NSPS
subpart J Refinery Fuel Gas.
Abstract for [1200041]
Q: Does EPA approve an alternative
monitoring request for monitoring
hydrogen sulfide (H2S) the No. 4 vent
stream at the Valero Refining West Plant
in Corpus Christi, Texas? The request
involves vent streams from the Oleflex
Reactor Lock Hopper Engager off-gas
vent stream combusted at the Oleflex
Interheater.
A: Yes. EPA approves Valero’s
alternative monitoring request based on
the description of the process vent
stream, the design of the vent gas
controls, and the H2S monitoring data
furnished. There will be no points
where sour gas can be introduced into
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the vent gas stream. The effluent is to be
sampled and tested daily. Valero must
follow the seven step process
(Alternative Monitoring Plans for NSPS
subpart J Refinery Fuel Gas) in the
consent decree for the No. 4 vent
stream.
Abstract for [1200042]
Q: Does EPA approve an Alternative
Monitoring Plan (AMP) for monitoring
hydrogen sulfide (H2S) of vent gases
from the control of diesel and jet fuel
truck loading, toluene and reformate
storage tanks, and groundwater recovery
wells at the Valero Refining Corpus
Christi, Texas East refinery? The vent
streams are combusted at the truck rack
thermal oxidizer enclosed vapor
combustor.
A: Yes. EPA approves Valero’s AMP
based on the description of the process
vent stream, the design of the vent gas
controls, and the H2S monitoring data
furnished. Valero must follow the seven
step process detailed in the Alternative
Monitoring Plans for NSPS subpart J
Refinery Fuel Gas appendix of Valero’s
consent decree. The approval specifies
an H2S operating limit from each of the
emission sources (e.g., loading, tanks,
wells) covered by the AMP.
Abstract for [1200046]
Q: Does EPA approve single-point
testing in place of Method 1 or 1A for
required testing of engine emissions
under 40 CFR part 60 subpart JJJJ, for
the ConocoPhillips Lake Pelto
Compressor Barge, located offshore in
southern Louisiana?
A: Yes. EPA approves ConocoPhillips’
single-point testing, since the engines
are located over water, and are difficult
to test due to limited space.
Abstract for [1200062]
Q1: Is the installation of a backup
vapor recovery unit (BU–VRU) to
capture emissions from a glycol
dehydrator unit, which includes a
compressor, at the Marathon Petroleum
Indian Basin Gas Plant near Carlsbad,
New Mexico, considered a modification
of an affected facility and thus subject
to NSPS subpart KKK?
A1: Based on the information
provided by the Air Quality Bureau of
the New Mexico Environment
Department (AQB–NMED), EPA
determines that the installation of the
BU–VRU compressor at the Indian Basin
Gas Plant is subject to NSPS subpart
KKK. The compressor is an affected
facility under NSPS subpart KKK that
was constructed after the applicability
date and is presumed to be in VOC or
wet gas service. The pollution control
device exemption in 40 CFR 60.14(e) of
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the General Provisions is superseded by
40 CFR 60.630 and therefore does not
apply. In addition, the NSPS subpart
KKK does not include exemptions for
compressor emergency operations or
operating less than 500 hours per year.
With respect to whether the other
affected facility, which includes all
other equipment (except compressors),
that are part of the glycol dehydrator
process unit, EPA cannot make a
modification determination since there
is no information on emission increases
or decreases available.
Q2: Are the two storage tanks at the
Indian Basin Gas Plant subject to NSPS
subpart Kb, or are they exempt under
the custody transfer exemption in 40
CFR 60.110b(d)(4)?
A2: Based on the information
provided by AQB–NMED, EPA
determines that the storage tanks are
subject to NSPS subpart Kb. The Indian
Basin Gas Plant is not part of the
producing operation and its tanks are
after the point of custody transfer as
defined at 40 CFR 60.111(b). Therefore,
the tanks do not qualify for the ‘‘prior
to custody transfer’’ exemption in 40
CFR 60.110b(d)(4).
Abstract for [M120027]
Q1: Does EPA agree with the
determinations of the Portsmouth Local
Air Agency and the Southeast District
Office of the Ohio EPA that the America
Styrenics Hanging Rock and Marietta,
Ohio facilities are subject to the MACT
if they changed processes after the
compliance date such that their
potential emissions are well below the
HAP major source thresholds?
A1: Yes. Based on the information
provided by the Portsmouth Local Air
Agency, EPA determines that the
facilities are still subject to the major
source MACT standard because it is
EPA’s position that any source that is a
major source of HAP on the first
substantive compliance date of an
applicable NESHAP will remain subject
to that NESHAP regardless of the level
of the source’s subsequent emissions.
Q2: Are these facilities still subject to
Title V if their HAP emissions potential
was the only criteria that made them
subject to Title V requirements?
A2: Yes. Because the facilities are
subject to a major source MACT
standard, they are also subject to Title
V permitting requirements under
Section 502(a) of the CAA, 42 U.S.C.
7661a(a).
Abstract for [M120029]
Q: Does EPA approve an alternative
monitoring frequency for inspections of
once per month rather than every 30
days under the Pulp and Paper MACT
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for Smurfit-Stone Container Corporation
in Coshocton, Ohio?
A: Yes. EPA approves this minor
modification to the monitoring
frequency under 40 CFR 63.8(b)(i)
provided that the monitoring events are
at least 21 days apart.
Abstract for [1200087]
Q: Does EPA approve a request to use
a subtractive method for the NOx
compliance determination and use of a
temporary Continuous Emission
Monitoring System (CEMs) for the
initial performance test for a NSPS
subpart Db affected facility at Valero
Refining’s Ethanol Plant in
Bloomingburg, Ohio? The proposed
method uses combined emissions from
this subpart Db facility and another
affected facility as determined by a
Continuous Emission Monitoring
System (CEMS), and subtracts the
emissions from the other facility as read
by a separate CEMS.
A: Yes. EPA approves the subtractive
compliance determination approach
under 40 CFR 60.8(b) authority for the
initial performance testing. This request
was necessary because, while the NSPS
allows for the location of a CEMS in a
stack serving multiple affected sources
for the purpose of demonstration of
continuous compliance, no such
allowance is made for the initial
performance testing requirement.
Abstract for [Z140004]
Q1: Are emergency engines located at
commercial sources that are used for
telecommunications purposes exempt
from the Reciprocating Internal
Combustion Engines (RICE) NESHAP
regulations at 40 CFR part 63, subpart
ZZZZ?
A1: Yes. The requirements at 40 CFR
part 63.6590(b)(3) state that emergency
engines located at area sources that are
classified as commercial, institutional or
residential emergency stationary RICE
are not subject to the requirements at 40
CFR part 63, subpart ZZZZ.
Q2: Are emergency engines used by
telecommunication facilities that are
installed and located on industrial
property also exempt?
A2: The applicability of the RICE
NESHAP is dependent on whether the
commercial or industrial operation has
common control over the emergency
engine. If the industrial facility has
control, the engine could be subject to
the RICE NESHAP.
Abstract for [1400016]
Q1: Is Kippur Corporation’s (Kippur)
dual chamber, commercial incinerator
which thermally destroys contraband
for U.S. Customs and Border Protection
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in El Paso, Texas subject to regulation
as an ‘‘other solid waste incineration’’
(OSWI) unit under 40 CFR part 60
subparts EEEE and FFFF?
A1: Yes. Based on the information
submitted by Kippur, EPA determines
that the contraband incinerator is an
OSWI unit subject to either NSPS
subpart EEEE or subpart FFFF. In
addition, the incinerator would not be
subject to subpart EEEE because an air
pollution abatement equipment is not
considered part of an OSWI unit.
Therefore, the increased feed rate
caused by the higher air flow volume
resulting from the addition of a second
baghouse on the OSWI unit does not
constitute a modification of the
incinerator under NSPS subpart EEEE.
Based on this and additional
supplemental information Kippur
provided, the OSWI Unit is therefore
subject to NSPS subpart FFFF since
subpart EEEE applicability was not
trigger with the OSWI unit changes
consistent with 40 CFR 60.2992.
Q2: Does EPA approve a petition for
approval of operating parameter limits
(OPLs) in lieu of installing a wet
scrubber to comply with emission
limitations?
A2: No. In a separate September 12,
2012 letter, EPA disapproved the
petition because specific information
was lacking for final approval.
Therefore, Kippur must comply with the
appropriate NSPS subpart FFFF
requirements.
Abstract for [1400019]
Q1: The Cornerstone Environmental
Group, LLC. on behalf of American
Disposal Services of Illinois, which
owns the Livingston Landfill, requests a
clarification as to whether the
Alternative Compliance Timeline (ACT)
requests are due 15 days after an initial
exceedance is identified through
required monitoring activities, pursuant
to the requirements in 40 CFR
60.755(a)(3) and (a)(s).
A1: EPA indicates that 40 CFR 60.755
requires landfill owner/operators to
repair the cause of an exceedance
within 15 days, or expand the gas
collection system within 120 days. In
the event that the landfill owner or
operator, despite its best efforts, is
unable to make the necessary repairs to
resolve the exceedance within 15 days,
and it believes that an expansion of gas
collection is unwarranted, the landfill
owner or operator may submit for
approval an ACT request for correcting
the as soon as possible (i.e., as soon as
it knows that it will not be able to
correct the exceedance in 15 days and
it is unwarranted to expand the gas
collection system) to avoid being in
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violation of the rule and communicate
the reasons for the exceedance, results
of the investigation, and schedule for
corrective action.
Q2: Are ACT requests necessary if the
owner/operator chooses to expand the
gas collection system and is unable to
complete the expansion project within
120 days?
A2: Yes. The landfill owner or
operator may submit an ACT request as
soon as it determines that it cannot meet
the 120 day deadline to avoid being in
violation of the rule. See above response
under A1.
Q3: What information is included in
an ACT request?
A3: EPA’s response describes a
number of items that should be
included, at a minimum. The request
must promptly identify the problem, be
very detailed, and contain substantial
reasons beyond the control of the
facility owner or operator why the
exceedances could not and cannot be
completed within the prescribed time
frame allowed in the rule.
Q4: If a facility makes repairs to a well
to restore the well field to its original
designed capacity, or replaces the well
in-kind, does that constitute an
expansion of the gas collection system
(thereby causing the 120-day deadline to
be applicable)?
A4: No. An expansion of the gas
collection system consists of an increase
beyond the original design capacity.
Abstract for [A140003]
Q1: Are bridges considered regulated
structures under the asbestos NESHAP?
A1: Yes. In a response to the
California Air Resource Board, EPA
indicated that a bridge is a structure
within the definition of a facility. As
discussed in the October 1990
Background Information Document for
Asbestos, it is prudent not to exclude
structures such as bridges.
Q2: Is a thorough inspection of a
bridge for the presence of asbestos,
including Category I and Category II,
required under the asbestos NESHAP?
A2: Yes. Under 40 CFR 61.145(a), a
thorough inspection of any facility is
required before demolition or
renovation to identify friable asbestos,
Category I and Category II nonfriable
asbestos-containing material (ACM) and
Category I and Category II nonfriable
ACM that are not friable at the time of
the inspection but will be made friable
due to the demolition or renovation.
Q3: Is bridge concrete Category I, or
is it Category II nonfriable ACM?
A3: Bridge concrete is not listed as
Category I nonfriable ACM. According
to 40 CFR 61.141, Bridge concrete is
considered Category II nonfriable ACM
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if it contains more than 1 percent
asbestos that, when dry, cannot be
crumbled, pulverized, or reduced to
powder by hand pressure.
Q4: Must bridge concrete be sampled
for the presence of asbestos before
demolition?
A4: The bridge concrete must be
thoroughly inspected. See 40 CFR
61.145(a). Sampling is done to
determine whether the material is ACM
or not. The amount of ACM that is or
will be made friable during the
demolition factors into whether asbestos
NESHAP requirements apply.
Q5: If the bridge concrete was never
tested for the presence of asbestos before
demolition and now the concrete is
going to be crushed and recycled, must
the concrete be tested for asbestos before
crushing and recycling?
A5: The concrete at a demolition
operation regulated by 40 CFR 61.145
must be thoroughly inspected before the
demolition operation to determine
whether the material is ACM. The
recycling could be considered part of
the demolition operation and require
the owner/operator to sample to
determine whether the concrete is ACM.
The results will determine whether the
concrete can continue to be recycled or
must be managed and disposed of as
regulated ACM.
Abstract for [M140006]
Q: Does K&K Ironworks in Chicago,
Illinois remain subject to 40 CFR part 63
subpart MMMM given that they no
longer use the quantity of coatings
required by 40 CFR 63.3881(b) for an
affected source to be covered by Subpart
MMMM, and they meet the criteria
established at 40 CFR 63.3881(c)(1) to be
excluded from coverage of subpart
MMMM?
A: Although K&K Ironworks of
Chicago operations no longer fall under
the types of activities subject to Subpart
MMMM, there may be requirements of
subpart MMMM and 40 CFR part 63
subpart A that did not immediately
terminate when the company
discontinued the use of coatings that
contain HAPs. For example, the records
retention and recordkeeping
requirements at 40 CFR 63.3931(b) and
63.10(b)(3) are continuing obligations,
that were triggered when the company
used xylene.
Abstract for [M140008]
Q: Frontier Refining requested an
applicability determination regarding
the timing of tank inspections to meet
the annual tank inspection requirements
under NESHAP subpart G for the Holly
Frontier facility in Wyoming. Can the
annual inspection requirement be
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accomplished within an 11–13 month
window from the prior inspection?
A: Yes. If a regulation does not
specifically state what is meant by the
‘‘once per’’ (timeframe), the EPA
interprets the timeframe to mean at
some point within the timeframe and at
a reasonable interval between events.
See, for example, 40 CFR
63.100(k)(9)(iii). A once per month
obligation means sometime within the
month, but not the last day of one
month and the first day of the next
month, because that is not a reasonable
time interval. For annual requirements,
a reasonable interval between events
would be between 11 and 13 months.
Abstract for [1400021]
Q: Does EPA agree that Calumet
Superior’s two steam generating boilers
located at its petroleum refinery in
Superior, Wisconsin, and which are fuel
gas combustion devices (FGCDs)
affected facilities under NSPS subpart
Ja, do not meet the definition of a
process heaters under NSPS subpart Ja,
and therefore are not subject to the
emission limits, performance testing,
monitoring and excess emission
reporting requirements for NOx located
at 40 CFR 60.102a(g)(2), 60.104a(i),
60.107a(c), 60.107a(d) and 60.102a(i)?
A: Yes. EPA agrees that Calumet
Superior’s boilers meet the definition of
FGCDs and do not meet the definition
of process heaters under NSPS subpart
Ja. Therefore, the boilers are not subject
to any NOx requirements under NSPS
subpart Ja. However, to the extent that
the boilers are affected facilities under
the Standards of Performance for Small
Industrial-Commercial-Institutional
Steam Generating Units, NSPS subpart
Dc, they may be subject to NOx
requirements.
Abstract for [M140009]
Q: May Benson Woodworking in
Walpole, New Hampshire de-rate its
Caterpillar 3306 Generator Set from its
current capacity of greater than 300
brake horsepower hour (bhp) to less
than 300 bhp by cutting the existing
factory governor seal, resetting the
loading screws to the lower output
specification, and then resealing the
governor with wire and a dealer specific
lead stamp, to comply with the
Reciprocating Internal Combustion
Engines (RICE) NESHAP regulations at
40 CFR part 63, subpart ZZZZ?
A: No. The de-rate method proposal is
not approvable by EPA. The proposed
method of de-rating the engine is not
permanent in nature.
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Abstract for [M140010]
Q: Can the following physical changes
to Benson Woodworking’s Walpole,
New Hampshire Caterpillar 3306
Generator Set, including: removal of the
current 400 amp circuit breaker and
associated frame; destruction of the 400
amp frame; and, fabrication and
installation of a new frame to hold a
smaller 250 amp circuit that would
prevent the engine output from
exceeding 299 bhp, result in a de-rating
of engine’s capacity to less than 300
bhp?
A: Yes. Based on the physical changes
that Benson has proposed, EPA
approves the de-rating of the unit to less
than 300 bhp given the permanent
nature of the physical changes to the
unit.
Abstract for [M140011]
Q: Does the NSPS for Stationary
Compression Ignition Internal
Combustion Engines, subpart IIII apply
to an existing marine propulsion engine
manufactured March 22, 1999 (EU ID#4)
that the Alaska Village Electric
Cooperative (AVEC) is planning to
relocate as a non-stationary engine at its
existing power plant in Emmonak,
Alaska?
A: No. The EU ID#4 engine is not
subject to NSPS subpart IIII because it
was manufactured prior to April 1,
2006, and commenced construction
prior to July 11, 2005. The conversion
of an existing non-stationary engine to
use as an engine at a stationary source
is not ‘‘commencement of construction’’
that would trigger new source status
under this rule. However, the EU ID#4
existing engine would be subject to the
NESHAP for Stationary Reciprocating
Internal Combustion Engines (RICE), 40
CFR part 63 subpart ZZZZ when it is
operated as a stationary source.
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Abstract for [M140012]
Q1: Did a force majeure event, as
defined in 40 CFR part 63 subpart A,
occur at the Chena Power Plant in
Fairbanks, Alaska?
A1: Yes. EPA determines that on
April 28, 2014, a force majeure event
occurred at the Chena Power Plant in
Fairbanks, Alaska, when a mechanical
failure of one of the facility’s turbine
generator rendered it inoperable.
Q2: Is a 60 day extension of the
performance test deadline under
NESHAP subpart JJJJJJ appropriate?
A2: Yes. The turbine generator, which
is subject to a testing deadline, is
needed for representative operation of
the boiler when the load from winter
district heating is not there to draw
steam from the boiler. In 60 days
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(November 17, 2014) the load from
winter district heating will be sufficient.
Considering the time estimated to repair
the turbine generator, it is reasonable to
extend the deadline for the boiler
compliance testing by 60 days.
Abstract for [M140013]
Q: Can EPA provide further guidance
on how to conduct tune-ups under 40
CFR 63.11223(b), which is Condition 4
of the previously EPA approved oneyear compliance deadline extension for
the Eielson Air Force Base’s Central
Heat and Power Plant in Alaska? The
four existing coal fired boilers subject to
the compliance extension are of the
spreader stoker/traveling grate design
and do not have burners.
A: Yes. EPA amends the previous
approval of the compliance extension to
provide further guidance on Condition 4
of the approval, as detailed in the EPA
response letter. EPA provides guidance
on how to meet the requirements of 40
CFR 63.11223(b) when burners are not
present. Some requirements of 40 CFR
63.11223(b) do not apply, while others
requirements, such as adjusting the airto-fuel ratio, and measurement of
oxygen and carbon monoxide are still
required to be performed.
Abstract for [M140014]
Q: Does EPA approve a one-year
compliance extension to meet the
NESHAP for Area Sources: Industrial,
Commercial and Institutional Boilers,
subpart JJJJJJ, for three existing coalfired boilers (that operate as back-ups)
located at the Brigham Young
University in Idaho (BYU-Idaho)? The
coal-fired boilers will be demolished
and replaced with a new energy plant
that will be fueled with natural gas.
A: EPA conditionally approves an
extension until December 31, 2014, to
operate three coal-fired boilers in their
backup capacity without the installation
of controls that would otherwise be
required to meet the NESHAP subpart
JJJJJ. The compliance deadline is
extended because BYU-Idaho is
constructing a natural gas source of
energy generation as a replacement
source of energy to meet requirements of
the CAA standard. The approval is
conditional on BYU-Idaho
implementing: (1) interim compliance
deadlines for the construction of the
natural gas replacement energy; and (2)
tune-ups specified in 40 CFR 63.11214
for existing coal-fired boilers with a heat
input capacity of less than 10 MM BTU/
hr that do not meet the definition of
limited-use boiler, or an oxygen trim
system that maintains an optimum airto-fuel ratio.
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Abstract for [Z140007]
Q: Which area source NESHAP
regulation applies to the operations at
the BASF Corporation Facility in
Lancaster, Texas (Lancaster site)? The
NESHAP regulations to evaluate
include: NESHAP subpart BBBBBBB
applicable to Chemical Preparations
Industry area source category; NESHAP
subpart VVVVVV applicable to the
Chemical Manufacturing Source
Category; and NESHAP subpart
CCCCCCC applicable to Paints and
Allied Products Manufacturing.
A: EPA finds that the NESHAP
subpart BBBBBBB is applicable because
the operations at the Lancaster site are
mixing-type processes, which are
typical of the Chemical Preparations
Source Category. EPA understands the
Lancaster Site produces architectural
coatings, primarily acrylic latex-based
stucco that contains aggregate, primarily
sand. The Lancaster Site mixes latex
dispersions produced off-site with
aggregate and other additives to produce
acrylic-based stucco.
Abstract for [A140004]
Q: Does EPA agree with the City of
Sarasota, Florida that the demolition of
a single-family residential building
acquired by the city is not subject to the
asbestos NESHAP subpart M due to the
small residence exemption?
A: Yes. Based on facts presented in
the Memorandum of Law from Sarasota
and the definition of facility in the
asbestos NESHAP, EPA determines the
building meets the conditions of a small
residential building (a building
containing four or fewer dwelling units)
and is not subject to the asbestos
NESHAP regulation. The house was not
used for any institutional, commercial,
public, or industrial purpose prior to the
demolition. It is not part of an
installation, nor part of any public or
private project.
Abstract for [A140005]
Q: Does EPA approve the
Transmission Electron Microscopy test
procedure in place of the point counting
procedure used to make a determination
of the presence of asbestos in bulk
materials, as required under the asbestos
NESHAP?
A: In a response to Masek Consulting
Services, EPA indicates that the current
asbestos regulation requires point
counting after evaluating the sample by
Polarized Light Microscopy. The owner/
operator may choose to use
Transmission Electron Microscopy only
after analyzing the sample by Polarized
Light Microscopy and point counting.
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Abstract for [M140016]
Q: Does EPA agree that the Boise
DeRidder Mill No. l Bark Boiler in
DeRidder, Louisiana is a biomass hybrid
suspension grate boiler under NESHAP
subpart DDDDD?
A: Yes. EPA agrees that the boiler is
subject to NESHAP subpart DDDDD.
The Bark Boiler has characteristics that
are consistent with the definition of
hybrid suspension grate boiler at 40 CFR
63.7575. However, natural gas and tire
derived fuel are also present as potential
fuels in the boiler. Therefore, the facility
must keep records to demonstrate that
the annual average moisture content is
at or above the 40 percent moisture
limit, as required in the rule.
tkelley on DSK3SPTVN1PROD with NOTICES
Abstract for [1400022]
Q: Does EPA approve the alternative
monitoring plan (AMP) for product
vapors from marine vessel loading
operations which are inherently low in
sulfur content, and are combusted in the
Marine Vapor Recovery (MVR) Flare
No.3, under NSPS 40 CFR 60 subpart J
for the Chalmette Refining’s Chalmette,
Louisiana refinery?
A: EPA determines that the AMP is no
longer necessary since the definition of
fuel gas has been modified under the
September 12, 2012 amendment to
subpart J (77 Federal Register 56463).
The marine vessel loading vapor stream
does not meet the definition of a fuel
gas, as defined at 40 CFR 60.101(d).
Therefore, MVR Flare No.3 does not
need to meet the continuous monitoring
requirements of either 40 CFR
60.105(a)(3) or 60.105(a)(4).
Abstract for [1400023]
Q: Can an exemption from monitoring
be approved for a fuel gas stream that
is low in sulfur content under NSPS
subpart J, for the off-gas vent stream
from the Gasoline Desulfurization Unit
Selective Hydrogenation Unit Surge
Drum Vent that is routed to the North
Flare at the Marathon Oil facility in
Garyville, Louisiana?
A: Yes. Based on Marathon’s
description of the process vent streams,
the design of the vent gas controls, and
the H2S monitoring data furnished, EPA
conditionally approves the exemption.
EPA finds that, when controlled as
delineated in the response letter, the
vent gas stream combusted is inherently
low in sulfur, according to 40 CFR
60.105(a)(4)(iv)(D), and does not need to
meet the continuous monitoring
requirements of 40 CFR 60.105(a)(3) or
60.105(a)(4). EPA included the facility’s
proposed operating parameter limits,
which the facility must continue to
monitor, as part of the conditional
approval.
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Abstract for [1400024]
Q: Can an exemption in lieu of
Alternative Monitoring Plan be
approved for a fuel gas stream that is
low in sulfur under NSPS 40 CFR 60
subpart J at the ExxonMobil refinery in
Baytown, Texas? The refinery proposes
to combust commercial grade natural
gas as a supplemental fuel, in
combination with refinery fuel gas vent
streams.
A: Yes. Based on ExxonMobil’s
description of the process vent streams,
the design of the vent gas controls, and
the H2S monitoring data furnished, EPA
conditionally approves the exemption.
EPA finds that the mixture of nonmonitored commercial natural gas and
refinery fuel vent gas stream combusted
is inherently low in sulfur, according to
40 CFR 60.105(a)(4)(iv)(D), when used
and controlled as described in the EPA
response letter. EPA included the
facility’s proposed operating parameter
limits, which the facility must continue
to monitor, as part of the conditional
approval. Therefore, the fuel gas
combustion devices listed in the request
do not need to meet the continuous
monitoring requirements of 40 CFR
60.105(a)(3) or 60.105(a)(4).
Abstract for [1400025]
Q: Is the propane refrigeration system
used at the Enbridge Nine Mile Gas
Plant in Dewey County, Oklahoma
subject to the requirements of NSPS 40
CFR 60 subpart KKK?
A: Yes. EPA determines that propane
system is subject to NSPS KKK based
upon the information the company
provided. The propane refrigeration
system is a process unit that can also
operate independently if supplied with
sufficient feed. The propane
refrigeration system is ‘‘equipment’’
under 40 CFR 60.631 because it consists
of valves, connectors, and compressors
in VOC service. These components are
in light liquid VOC service because they
contain or contact propane, which
constitutes at least 97 percent by weight
of content of the refrigeration system,
and the propane is a liquid within the
operating conditions of the refrigeration
system.
Abstract for [1400026]
Q: Are two natural gas reciprocating
compressors which were transferred
from a ‘‘laydown’’ yard to the
Fayetteville Gathering Hattieville
Compressor Station, located in
Hattieville, Arkansas, affected facilities
subject to the requirements of NSPS
subpart OOOO?
A: No. Relocation, by itself, does not
trigger NSPS applicability through
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Sfmt 4703
modification. Based upon the fact that
the company commenced construction
of the two compressors on a continuous
basis prior to the effective date of NSPS
subpart OOOO, nor were they modified,
these units are not affected facilities
under the subpart. EPA clarified in final
rule preamble to NSPS OOOO that
relocation does not subject a source to
new source standards. Additionally, the
General Provisions to Part 60 contain
similar language, that relocation or
change in ownership, by itself, is not a
modification.
Abstract for [1400027]
Q1: Does EPA provide final approval
of an Alternative Monitoring Plan
(AMP) for parametric monitoring in lieu
of a continuous opacity monitor for a
Wet Gas Scrubber (WGS) on a Fluidized
Catalytic Cracking Unit (FCCU) at Holly
Refining & Marketing in Tulsa,
Oklahoma (Holly) under NSPS 40 CFR
60, subpart J, and NESHAP 40 CFR 63,
subpart UUU, based on submittal of test
results?
A1: Yes. EPA grants final approval of
Holly’s AMP request. Holly conducted a
performance test and submitted
additional data pertaining to a prior,
conditionally approved AMP. EPA
reviewed the performance test results
and found the data supportive for
establishing final OPLs for the WGS,
which included minimum Liquid-to-Gas
Ratios, based on 3-hour, hourly rolling
averages, for operation of the WGS with
one or two nozzles.
Abstract for [1400028]
Q: May the Ineos Chocolate Bayou
facility in Alvin, Texas, which is subject
to both 40 CFR part 60, Standards of
Performance for Volatile Organic
Compound (VOC) Emissions from
Synthetic Organic Chemical
Manufacturing Industry (SOCMI)
Distillation Operations (NSPS subpart
NNN) and Reactor Processes (NSPS
subpart RRR) use the monitoring and
testing provisions in NSPS subpart RRR
in lieu of NSPS subpart NNN for the
process heaters?
A: Yes. EPA approves the request for
meeting Subpart RRR in lieu of NSPS
subpart NNN requirements for testing,
monitoring, and recordkeeping for use
of process heaters as control devices for
compliance with the standards of both
subparts. This would require monitoring
of small vent and drain valves utilized
for maintenance events during
maintenance in accordance with NSPS
subpart RRR since they act as bypass
valves. In addition, the schematic
required by 40 CFR 60.705(s) is required
with the initial report and must be
maintained on site to ensure that the
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affected vent streams are being routed to
appropriate control devices without
bypass.
Abstract for [1400029]
Q1: Does EPA agree with Kinder
Morgan that the Condensate Splitter
Flare located at the Galena Park
Condensate Processing Facility in Harris
County, Texas is subject to NSPS
subpart Ja?
A1: No. EPA is unable to verify
applicability of NSPS subpart Ja because
sufficient information about the facility
or the operations and processes vented
to the flare were not provided.
Q2: Does EPA approve an Alternative
Monitoring Plan (AMP) request for the
Condensate Splitter Flare?
A2: No. Kinder Morgan did not
furnish sufficient detail about vent
streams routed to the flare, or
adequately describe the specific refinery
process that would produce low sulfur
content vent streams. Assuming the vent
streams are fuel gas streams subject to
NSPS subpart Ja, we cannot approve any
AMP that seeks to circumvent a specific
emissions monitoring requirement for
affected facility operations. Under
NSPS, new facilities must be
constructed in such a manner that
monitors are installed to demonstrate
initial compliance and ensure ongoing
compliance until such time that an
exemption can be met. Furthermore,
applications for exemptions to a rule
must provide sufficient data at the time
of the request in order to be evaluated
for approval.
tkelley on DSK3SPTVN1PROD with NOTICES
Abstract for [1400030]
Q1: Does EPA approve the
HollyFrontier Companies’ request for
approval of an Alternative Monitoring
Plan (AMP) for monitoring oxygen in
the stack, in lieu of parametric
monitoring to substitute for a
Continuous Emissions Monitoring
System, for the hydrocracker reboiler at
Navajo Refining’s Artesia, New Mexico
refinery (Navajo), to comply with the
NOX and oxygen standards in NSPS, 40
CFR part 60 subpart Ja?
A1: Yes. EPA determines that
Navajo’s AMP that combines monitoring
oxygen in the stack along with other
specific process monitoring parameters
is acceptable based on the limited usage
of refinery fuel gas and the information
submitted, including the performance
test results. Navajo sampled the fuel gas
at the reboiler to demonstrate that the
stream is 100 percent purchased natural
gas. Also, to improve the efficiency of
the heater, Navajo installed new burner
tips to better combust the purchased
natural gas. As a result, NOX and O2
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emissions were reduced, as verified by
a performance test.
Abstract for [1400031]
Q: Does EPA approve an Alternative
Monitoring Plan (AMP) for PSC
Industrial to conduct monitoring of H2S
emissions at various locations in EPA
Region 6, in lieu of installing a
continuous emission monitoring system
(CEMS), when performing tank
degassing and other similar operations
controlled by portable, temporary
thermal oxidizers, at refineries that are
subject to NSPS 40 CFR 60 subparts J or
Ja?
A: Yes. EPA conditionally approves
PSC Industrial’s AMP request. Based on
the description of the process, the vent
gas streams, the design of the vent gas
controls, and the H2S monitoring data
furnished, EPA finds that it is
impractical to require monitoring via an
H2S CEMS as specified by NSPS
subparts J and Ja for the specific
portable and temporary combustion
device use. EPA included operating
parameter limits (OPLs) and data which
the refineries must furnish as part of the
conditional approval. This conditional
approval applies to this company’s
refineries in EPA Region 6 only. EPA’s
conditional approval should also be
referenced and appropriately
incorporated into PSC Industrial’s new
source review permit in each state
where degassing operations at refineries
will occur, to ensure federal
enforceability.
Abstract for [1400032]
Q: Can Samson Exploration, Houston,
Texas submit hard copy photographs
with the required GIS and date stamp
data printed below each photograph in
streamlined annual reports required
under 40 CFR 60.5420(b)(2) of NSPS
subpart OOOO?
A: Yes. The inclusion of such types of
submissions in annual reports is
acceptable. There is no regulatory
prohibition against submitting hard
copies which have the date and GIS
coordinates printed beneath each
photograph, provided that the proximity
of each photograph and its associated
data ensures clear correlation. EPA
further clarified that, in conjunction
with the self-certification statement
required under 40 CFR 60.5420(b)(1)(iv),
a statement should be included that
digital images of the photographs for
each well completion are retained, such
that the digital image files contain
embedded date stamps and geographic
coordinate stamps to link the
photographs with the specific well
completion operations.
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Sfmt 4703
22185
Abstract for [1400033]
Q: Can EPA approve an Alternative
Monitoring Plan (AMP) for Tristar
Global Energy Solutions Company
(Tristar) to conduct monitoring of
hydrogen sulfide (H2S) emissions, in
lieu of installing a continuous emission
monitoring system, when performing
tank degassing and other similar
operations controlled by portable,
temporary thermal oxidizers, at
refineries at various locations that are
subject to NSPS subparts J or Ja?
A: Yes. Based on the description of
the process, the vent gas streams, the
design of the vent gas controls, and the
H2S monitoring data furnished, EPA
conditionally approves the AMP
request. EPA included operating
parameter limits and data which the
refineries must furnish as part of the
conditional approval. This conditional
approval applies to Tristar’s degreasing
operations at refineries in EPA Region 6
only.
Abstract for [1400034]
Q1: Does EPA agree with Western
Farmers Electric Cooperative (WFEC)
that excess emission for the Hugo
Generating Station, Choctaw County,
Oklahoma coal-fired boiler, an ‘‘affected
facility’’ under NSPS for Fossil Fuel
Fired Steam Generators, subpart D,
would only be reported for certain
periods of operational status such as
when the boiler is firing fuel for the
purpose of generating electricity?
A1: No. EPA disagreed that reporting
of excess emissions should be limited to
certain periods of boiler operational
status. EPA reiterated that the NSPS
requires reporting of all periods of
excess emissions, including those
temporary occurrences that may result
in a particular emission standard being
exceeded. Required recordkeeping and
reporting should be viewed, along with
O&M and SSM protocols, as a
company’s substantiation of acting in
good faith to demonstrate compliance
with emission limitations, standards,
and work practice standards at all times.
EPA believes that WFEC has
misinterpreted certain monitoring,
recordkeeping and reporting provisions
in the NSPS and MACT standards that
a combustion source must meet for
continuous compliance demonstration,
which we explained in the Regulatory
Interpretation enclosure of the EPA
response.
Abstract for [1400035]
Q: Does EPA approve the alternative
monitoring Operating Parameter Limits
(OPLs) under NSPS subpart Ec, for a
pollution control system on a new
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medical waste incinerator which
consists of a wet gas scrubber (WGS)
followed by a carbon adsorber and
cartridge filter, located at the University
of Texas Medical Branch (UTMBG) in
Galveston, Texas?
A: Yes. EPA conditionally approves
Hydro-Environmental Technologies
petition on behalf UTMBG for an AMP.
As part of the conditional approval,
performance testing must be conducted
to demonstrate compliance and
establish OPL values for the WGS,
carbon adsorber and cartridge filter.
Final approval of the AMP will be based
on the OPLs established and other
provisions that may be deemed
necessary from our evaluation of the test
results.
tkelley on DSK3SPTVN1PROD with NOTICES
Abstract for [1400036]
Q: Will EPA approve the Fuel
Analysis Plan for monitoring total sulfur
content of fuels in lieu of SO2 emissions
monitoring under NSPS subpart Db for
Industrial-Commercial Institutional
Steam Generating Units for which
construction, reconstruction, or
modification commenced after June 19,
1984, at the No. 6 Power Boiler in
Westvaco, Texas L.P. facility
(Westvaco)?
A: Yes. EPA conditionally approves
Westvaco’s Fuel Analysis Plan, as
delineated within the response letter. 40
CFR 60.45b(k) allows compliance to be
demonstrated by a fuel based
compliance alternative. The plan
ensures that data will be collected to
demonstrate that the average percentage
sulfur concentration in the wood fuel,
plus three standard deviations, will not
result in a combined fuel mixture that
will exceed the sulfur emission limit.
Westvaco will continue to obtain and
maintain fuel receipts for the other
combusted fuels.
Abstract for [1400037]
Q: Can an exemption from monitoring
be approved for a fuel gas stream that
is low in sulfur content, under NSPS
subpart J, for the off-gas vent stream
from the Merox Off-gas Knockout Pot in
the Alky Stripper Reboiler Heater, at the
Valero Refining Meraux facility in
Meraux, Louisiana?
A: Yes. Based on the description of
the process vent streams, the design of
the vent gas controls, and the H2S
monitoring data furnished, EPA
conditionally approves the exemption
in light of changes made to NSPS
subpart J on June 24, 2008 (73 Federal
Register 35866). EPA finds that, when
used and controlled as described in the
response letter, the vent gas stream
combusted is inherently low in sulfur
according to 40 CFR 60.105(a)(4)(iv)(D)
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18:07 Apr 20, 2015
Jkt 235001
and therefore, the fuel gas combustion
device does not need to meet the
continuous monitoring requirements of
40 CFR 60.105(a)(3) or 60.105(a)(4) for
the Merox Off-gas Knockout Pot fuel gas
stream. Valero Meraux is required to
monitor and control the relevant process
parameters, as summarized in the
Enclosure, as a condition of this
exemption approval.
Abstract for [1100017]
Q: Can alternative monitoring be
approved in lieu of a Continuous
Opacity Monitoring System (COMS)
since the moisture in the Fluid Catalytic
Cracking Unit exhaust from the wet gas
scrubber (WGS) will interfere with the
ability of the COMS to take accurate
opacity readings due to water
interference for the Conoco Phillips
Sweeny, Texas Refinery?
A: Yes. EPA approves the alternative
monitoring based on information
provided by Conoco, including a stack
test report and three proposed operating
parameters limits (OPLs) for the wet gas
scrubber. The OPLs address nozzle
pressure, pressure drop, and liquid to
gas ratio.
Dated: April 13, 2015.
Lisa Lund,
Director, Office of Compliance.
includes whether the acquisition of the
nonbanking company complies with the
standards in section 4 of the BHC Act
(12 U.S.C. 1843). Unless otherwise
noted, nonbanking activities will be
conducted throughout the United States.
Unless otherwise noted, comments
regarding each of these applications
must be received at the Reserve Bank
indicated or the offices of the Board of
Governors not later than May 15, 2015.
A. Federal Reserve Bank of Chicago
(Colette A. Fried, Assistant Vice
President) 230 South LaSalle Street,
Chicago, Illinois 60690–1414:
1. Wintrust Financial Corporation,
Rosemont, Illinois; to acquire North
Bank, Chicago, Illinois.
B. Federal Reserve Bank of Dallas
(Robert L. Triplett III, Senior Vice
President) 2200 North Pearl Street,
Dallas, Texas 75201–2272:
1. First Financial Bankshares, Inc.,
Abilene, Texas; to merge with FBC
Bancshares, Inc., and thereby indirectly
acquire First Bank, National
Association, both in Conroe, Texas.
Board of Governors of the Federal Reserve
System, April 15, 2015.
Michael J. Lewandowski,
Associate Secretary of the Board.
[FR Doc. 2015–09021 Filed 4–20–15; 8:45 am]
BILLING CODE 6210–01–P
[FR Doc. 2015–09242 Filed 4–20–15; 8:45 am]
BILLING CODE 6560–50–P
FEDERAL RESERVE SYSTEM
FEDERAL RESERVE SYSTEM
Agency Information Collection
Activities: Announcement of Board
Approval Under Delegated Authority
and Submission to OMB
Formations of, Acquisitions by, and
Mergers of Bank Holding Companies
The companies listed in this notice
have applied to the Board for approval,
pursuant to the Bank Holding Company
Act of 1956 (12 U.S.C. 1841 et seq.)
(BHC Act), Regulation Y (12 CFR part
225), and all other applicable statutes
and regulations to become a bank
holding company and/or to acquire the
assets or the ownership of, control of, or
the power to vote shares of a bank or
bank holding company and all of the
banks and nonbanking companies
owned by the bank holding company,
including the companies listed below.
The applications listed below, as well
as other related filings required by the
Board, are available for immediate
inspection at the Federal Reserve Bank
indicated. The applications will also be
available for inspection at the offices of
the Board of Governors. Interested
persons may express their views in
writing on the standards enumerated in
the BHC Act (12 U.S.C. 1842(c)). If the
proposal also involves the acquisition of
a nonbanking company, the review also
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Board of Governors of the
Federal Reserve System.
SUMMARY: Notice is hereby given of the
final approval of proposed information
collection by the Board of Governors of
the Federal Reserve System (Board)
under OMB delegated authority, as per
OMB Regulations on Controlling
Paperwork Burdens on the Public.
Board-approved collections of
information are incorporated into the
official OMB inventory of currently
approved collections of information.
Copies of the Paperwork Reduction Act
Submission, supporting statements and
approved collection of information
instrument(s) are placed into OMB’s
public docket files. The Federal Reserve
may not conduct or sponsor, and the
respondent is not required to respond
to, an information collection that has
been extended, revised, or implemented
on or after October 1, 1995, unless it
displays a currently valid OMB control
number.
FOR FURTHER INFORMATION CONTACT:
Federal Reserve Board Acting Clearance
AGENCY:
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[Federal Register Volume 80, Number 76 (Tuesday, April 21, 2015)]
[Notices]
[Pages 22176-22186]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2015-09242]
=======================================================================
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ENVIRONMENTAL PROTECTION AGENCY
[FRL-9926-65-OECA]
Applicability Determination Index (ADI) Database System Recent
Posting: Applicability Determinations, Alternative Monitoring
Decisions, and Regulatory Interpretations Pertaining to Standards of
Performance for New Stationary Sources, National Emission Standards for
Hazardous Air Pollutants, and the Stratospheric Ozone Protection
Program
AGENCY: Environmental Protection Agency (EPA).
ACTION: Notice of availability.
-----------------------------------------------------------------------
SUMMARY: This notice announces applicability determinations,
alternative monitoring decisions, and regulatory interpretations that
EPA has made under the New Source Performance Standards (NSPS); the
National Emission Standards for Hazardous Air Pollutants (NESHAP); and/
or the Stratospheric Ozone Protection Program.
FOR FURTHER INFORMATION CONTACT: An electronic copy of each complete
document posted on the Applicability Determination Index (ADI) database
system is available on the Internet through the Resources and Guidance
Documents for Compliance Assistance page of the Clean Air Act
Compliance Monitoring Web site under ``Air'' at: https://www2.epa.gov/compliance/resources-and-guidance-documents-compliance-assistance. The
letters and memoranda on the ADI may be located by control number,
date, author, subpart, or subject search. For questions about the ADI
or this notice, contact Maria Malave at EPA by phone at: (202) 564-
7027, or by email at: malave.maria@epa.gov. For technical questions
about individual applicability determinations or monitoring decisions,
refer to the contact person identified in the individual documents, or
in the absence of a contact person, refer to the author of the
document.
SUPPLEMENTARY INFORMATION:
Background
The General Provisions of the NSPS in 40 Code of Federal
Regulations (CFR) part 60 and the General Provisions of the NESHAP in
40 CFR part 61 provide that a source owner or operator may request a
determination of whether certain intended actions constitute the
commencement of construction, reconstruction, or modification. EPA's
written responses to these inquiries are commonly referred to as
applicability determinations. See 40 CFR 60.5 and 61.06. Although the
part 63 NESHAP regulations [which include Maximum Achievable Control
Technology (MACT) and/or Generally Available Control Technology
(GACT)standards] and Sec. 111(d) of the Clean Air Act (CAA) contain no
specific regulatory provision providing that sources may request
applicability determinations, EPA also responds to written inquiries
regarding applicability for the part 63 and Sec. 111(d) programs. The
NSPS and NESHAP also allow sources to seek permission to use monitoring
or recordkeeping that is different from the promulgated requirements.
See 40 CFR 60.13(i), 61.14(g), 63.8(b)(1), 63.8(f), and 63.10(f). EPA's
written responses to these inquiries are commonly referred to as
alternative monitoring decisions. Furthermore, EPA responds to written
inquiries about the broad range of NSPS and NESHAP regulatory
requirements as they pertain to a whole source category. These
inquiries may pertain, for example, to the type of sources to which the
regulation applies, or to the testing, monitoring, recordkeeping, or
reporting requirements contained in the regulation. EPA's written
responses to these inquiries are commonly referred to as regulatory
interpretations.
EPA currently compiles EPA-issued NSPS and NESHAP applicability
determinations, alternative monitoring decisions, and regulatory
interpretations, and posts them to the
[[Page 22177]]
ADI. In addition, the ADI contains EPA-issued responses to requests
pursuant to the stratospheric ozone regulations, contained in 40 CFR
part 82. The ADI is an electronic index on the Internet with over one
thousand EPA letters and memoranda pertaining to the applicability,
monitoring, recordkeeping, and reporting requirements of the NSPS,
NESHAP, and stratospheric ozone regulations. Users can search for
letters and memoranda by date, office of issuance, subpart, citation,
control number, or by string word searches.
Today's notice comprises a summary of 56 such documents added to
the ADI on April 7, 2015. This notice lists the subject and header of
each letter and memorandum, as well as a brief abstract of the letter
or memorandum. Complete copies of these documents may be obtained from
the ADI through the OECA Web site at: www.epa.gov/compliance/monitoring/programs/caa/adi.html.
Summary of Headers and Abstracts
The following table identifies the database control number for each
document posted on the ADI database system on April 7, 2015; the
applicable category; the section(s) and/or subpart(s) of 40 CFR part
60, 61, or 63 (as applicable) addressed in the document; and the title
of the document, which provides a brief description of the subject
matter.
We have also included an abstract of each document identified with
its control number after the table. These abstracts are provided solely
to alert the public to possible items of interest and are not intended
as substitutes for the full text of the documents. This notice does not
change the status of any document with respect to whether it is ``of
nationwide scope or effect'' for purposes of CAA Sec. 307(b)(1). For
example, this notice does not convert an applicability determination
for a particular source into a nationwide rule. Neither does it purport
to make a previously non-binding document binding.
ADI Determinations Uploaded on April 7, 2015
----------------------------------------------------------------------------------------------------------------
Control Number Categories Subparts Title
----------------------------------------------------------------------------------------------------------------
M110015............................ MACT, PART 63 NESHAP, CC, G, Kb............. Rule Interpretation on Raw
NSPS. Data Definition and
Retention for Storage
Vessels.
1400038............................ NSPS.................. OOO................... Applicability of Rule to
Gypsum Handling Equipment
at a Power Plant with Fuel
Gas Desulfurization Units.
1100018............................ NSPS.................. J..................... Alternative Monitoring Plan
for Low Sulfur Bearing
Fuel Gas Stream.
Z140006............................ MACT, Part 63 NESHAP.. YYYYY................. Performance Test Waiver
Request for EAF Secondary
Dust Collection System.
M120012............................ MACT, PART 63 NESHAP.. FFFF.................. Alternative Monitoring Plan
For Grab Sampling in Lieu
of Continuous Monitoring
of Caustic Scrubbers.
Z120001............................ Part 61 NESHAP........ J, V.................. Applicability Determination
for NESHAP Subparts J and
V Benzene Fugitive
Equipment Leaks.
M120015............................ MACT, PART 63 NESHAP, J, UUU................ Alternate Work Practice--
NSPS. SRU Sulfur Pit Bypass
Lines.
Z140005............................ Part 63 NESHAP........ WWWWWW................ Applicability Determination
for Research and
Development Unit under
NESHAP Subpart WWWWWW.
M120018............................ MACT, PART 63 NESHAP, J, UUU................ Alternative Monitoring in
NSPS. Lieu of COMS for
Regenerators.
M120020............................ MACT, PART 63 NESHAP.. NNNNN................. Alternative Monitoring for
Caustic Scrubber
Parametric Monitoring.
1200038............................ NSPS.................. D..................... Stack COMS Relocation
Determined By Equivalency
Testing.
M120021............................ MACT, PART 63 NESHAP.. G, H.................. Approval of a Common Report
Schedule--MACT Subparts G
and H.
1200039............................ NSPS.................. J..................... Alternative Monitoring for
Hydrocracker Feed Surge
Drum Vent Stream.
1200040............................ NSPS.................. J..................... Alternative Monitoring for
NHT Feed Surge Drum Off--
Gas Vent Stream.
1200041............................ NSPS.................. J..................... Alternative Hydrogen
Sulfide Monitoring for
Oleflex Reactor Vent
Stream.
1200042............................ NSPS.................. J..................... Alternative Hydrogen
Sulfide Monitoring for
Truck Loading, Storage
Tank and Well Vent Gas
Streams.
1200046............................ NSPS.................. JJJJ.................. Single-Point Testing In
Place of Method 1 or 1A--
Engine Emission Testing.
1200062............................ NSPS.................. KKK, Kb............... Applicability of NSPS
Subparts Kb and KKK for a
Vapor Recovery Unit and
Storage Tanks.
M120027............................ MACT, PART 63 NESHAP.. JJJ................... Timing Issues in
Determining MACT and Title
V Applicability.
M120029............................ MACT, PART 63 NESHAP.. S..................... Approval of an Alternative
Monitoring Frequency under
the Pulp and Paper MACT.
1200087............................ NSPS.................. Db.................... Revision to NSPS Method of
Determining Compliance for
Combined Effluent NOX
CEMS.
Z140004............................ MACT, PART 63 NESHAP.. ZZZZ.................. Exemption for Emergency
Engines at Commercial Area
Sources from RICE NESHAP--
Regulatory Interpretation.
1400016............................ NSPS.................. EEEE, FFFF............ Applicability Determination
for Commercially Operated
Contraband Incinerator.
1400019............................ NSPS.................. WWW................... Guidance on Alternative
Compliance Timeline
Requests for Landfill.
A140003............................ Asbestos.............. M..................... Applicability of the
Asbestos NESHAP as it
Applies to Concrete
Bridges.
M140006............................ MACT, PART 63 NESHAP.. A, MMMM............... Continuing Requirements
when Surface Coating
Operations no Longer Meets
Affected Source Criteria.
M140008............................ MACT, PART 63 NESHAP.. CC, G................. Interpretation of Required
Tank Inspection Frequency.
1400021............................ NSPS.................. Dc, Ja................ NOx Requirements for
Boilers.
M140009............................ MACT, PART 63 NESHAP.. ZZZZ.................. Disapproval of an Engine De-
Rate Proposal.
M140010............................ MACT, PART 63 NESHAP.. ZZZZ.................. Approval of an Engine De-
rate Proposal.
[[Page 22178]]
M140011............................ MACT, PART 63 NESHAP, IIII, ZZZZ............ Applicability to a Non-
NSPS. stationary Engine
Relocated For Use as a
Stationary Engine.
M140012............................ PART 63 NESHAP........ A, JJJJJJ............. Determination of Force
Majeure.
M140013............................ PART 63 NESHAP........ JJJJJJ................ Regulatory Interpretation
of Tune-up Requirements
for Spreader Stoker
Boiler.
M140014............................ PART 63 NESHAP........ JJJJJJ................ Compliance Extension for
Replacement Energy Source.
Z140007............................ Part 63 NESHAP........ BBBBBBB, VVVVVV....... Rule Applicability to HAP-
Containing Mixing
Operations to Produce
Acrylic-Based Stucco.
A140004............................ Asbestos.............. M..................... Small Residence Exemption.
A140005............................ Asbestos.............. M..................... Interim Method of
Determination of Asbestos
in Bulk Insulation Samples
and Transmission Electron
Microscopy.
M140016............................ MACT, PART 63 NESHAP.. DDDDD................. Categorization and
applicability of a Boiler
using natural gas and tire
derived fuel.
1400022............................ NSPS.................. J..................... NSPS Fuel Gas Definition
and Alternative Monitoring
of Marine Vessel Loading
Vapors.
1400023............................ NSPS.................. J..................... Conditional CEMS Exemption
Approval for Low Sulfur
Combustion of Off-gas Vent
Stream.
1400024............................ NSPS.................. J..................... CEMS Exemption in Lieu of
Alternative Monitoring for
Combustion of Commercial
Grade Natural Gas and
Refinery Fuel Gas.
1400025............................ NSPS.................. KKK................... Regulatory Interpretation
for Gas Plant Propane
Refrigeration System.
1400026............................ NSPS.................. OOOO.................. Applicability Determination
for Reciprocating
Compressors.
1400027............................ MACT, PART 63 NESHAP, J, UUU................ Alternative Monitoring Plan
NSPS. for Wet Gas Scrubber on a
Fluidized Catalytic
Cracking Unit.
1400028............................ NSPS.................. NNN, RRR.............. Alternative Monitoring and
Waiver of Testing Request
for Distillation Vent Gas
to Process Heaters.
1400029............................ NSPS.................. Ja.................... Request for Alternative
Monitoring of Condensate
Splitter Flare.
1400030............................ NSPS.................. Ja.................... Alternative Monitoring Plan
for Oxygen in Boiler Stack
Emissions.
1400031............................ NSPS.................. J, Ja................. Alternative Hydrogen
Sulfide Monitoring in Tank
Degassing Vapors Combusted
in Portable Thermal
Oxidizers.
1400032............................ NSPS.................. OOOO.................. Regulatory Interpretation--
Submission of Photographs
For Natural Gas Well
Completion Annual Reports.
1400033............................ NSPS.................. J, Ja................. Alternative Hydrogen
Sulfide Monitoring in Tank
Degassing Vapors Combusted
in Portable Thermal
Oxidizers.
1400034............................ NSPS.................. A, D.................. Regulatory Interpretation--
Demonstrating Continuous
Compliance and Reporting
Excess Emissions for NSPS
and Title V.
1400035............................ NSPS.................. Ec.................... Alternative Operating
Parameters for a Wet Gas
Scrubber Followed By
Carbon Adsorber and
Cartridge Filter at an
HMIWI.
1400036............................ NSPS.................. Db.................... Alternative Monitoring Plan
for Fuel Analysis from
Subpart Db Boiler.
1400037............................ NSPS.................. J..................... Conditional CEMS Exemption
Approval for Low Sulfur
Combustion of Off-gas Vent
Stream.
1100017............................ NSPS.................. J..................... Alternative Monitoring of
Opacity for a Wet Gas
Scrubber.
----------------------------------------------------------------------------------------------------------------
Abstracts
Abstract for [M110015]
Q1: What is EPA interpretation of raw data, in reference to 40 CFR
63.654 and 40 CFR 60.115b and the storage vessel recordkeeping
provisions in NSPS subpart Kb, and Part 63 NESHAP subparts G and CC?
A1: EPA indicated to the Texas Commission on Environmental Quality
Region 14 that although the phrase ``raw data'' does not have a
regulatory definition, EPA has issued guidance on this subject to deal
with air pollution measurement systems and the quality assurance
procedures associated with such systems. In general, raw data is data
that is captured and recorded on field data sheets during a measurement
of some sort, such as sampling of emissions or testing of control
equipment.
Q2: May a source, after transferring data from field data sheets
into an electronic database, dispose of the field data sheets?
A2: No. Original field data sheets must be preserved whenever any
sort of emissions sampling or equipment testing, such as measuring seal
gaps in a storage tank, is performed. Transferring raw data into a
database can introduce additional error in data transcription and
entry.
Abstract for [1400038]
Q1: Is gypsum handling equipment at the Dominion Chesterfield Power
Station in Chester, Virginia, subject to NSPS subpart OOO for
Nonmetallic Mineral Processing Plants? Dominion acknowledges that a
limestone crushing process at Chesterfield is subject to subpart OOO.
A1: Yes. The gypsum handling equipment is also subject to NSPS
subpart OOO. The facility meets the definition of a nonmetallic mineral
processing plant, and each affected facility at Chesterfield is subject
to subpart OOO, including the belt conveyors used to transfer gypsum to
storage sheds or loading docks.
Q2: Must the crushing or grinding of gypsum take place in the
``production line'' to be subject to subpart OOO?
A2: No. The definition of production line does not require that
every affected facility be part of a production line with crushing or
grinding. If crushing or grinding of a nonmetallic mineral occurs
anywhere at the facility, then each affected facility is subject
regardless of its location within the plant.
Q3: Are there other power plants with flue gas desulfurization
units where the gypsum handling equipment is subject to subpart OOO?
A3: Yes. Based on a brief review of similar permits, EPA found at
least three such power plants with permits where subpart OOO was
applied to the gypsum handling equipment.
[[Page 22179]]
Abstract for [1100018]
Q: Does EPA approve the ConocoPhillips Sweeny, Texas Refinery
Alternate Monitoring Plan (AMP) under NSPS subpart J? Conoco claims an
exemption per 40 CFR 60.105(a)(4)(iv) because Flare #7 receives fuel
gas waste from catalytic reforming units.
A: Yes. EPA conditionally approves ConocoPhillips's AMP.
Conditional approval of alternative monitoring parameters is granted
based on a requirement that the flare receive low sulfur/sulfide
bearing streams waste fuel gas only from catalytic reformers. Any
significant increase in the sulfur/sulfide concentration detected in
the stream would initiate continuous monitoring under 40 CFR
60.105(a)(3) or (4). Introduction of other streams that are not from
catalytic reformers require application of another AMP.
Abstract for [Z140006]
Q1: Does EPA approve of a waiver in the number of performance test
sampling locations required to comply with particulate stack sampling
requirements under 40 CFR part 63 subpart YYYYY for the electric arc
furnace at ArcelorMittal's LaPlace, Louisiana facility?
A1: No. Based on the information provided, EPA could not approve
the request to sample only three of the six emission points. Without
the results of a previous performance test which included results for
all six emission points, EPA could not confirm that emissions from
three of the emission points might be representative of all six.
Additionally, EPA reserves the right to determine which emission points
should be sampled.
Q2: Can the 60-day testing notification requirement be waived,
allowing ArcelorMittal a 30-day notification period?
A2: Yes. Based on the timing of ArcelorMittal's testing waiver
request and the testing schedule, EPA is allowing a reduced testing
notification timeframe. EPA asked that ArcelorMittal provide the
Louisiana Department of Environmental Quality (DEQ) a written notice at
least ten (10) days prior to the intended testing dates in order that
DEQ be afforded the opportunity to observe the testing.
Abstract for [M120012]
Q: Does EPA approve the Alternative Monitoring Plan (AMP) for
monitoring the caustic strength of scrubber effluent by a grab sample
monitoring system, in lieu of continuously measuring caustic strength,
under MACT subpart FFFF for the miscellaneous organic chemical
manufacturing process units and caustic scrubbers controlling Group 1
Process Vents at the Dow Chemical plant in La Porte, Texas?
A: Yes. EPA approves the AMP based on the information provided. The
plan to monitor scrubber caustic strength by grab sampling, in lieu of
continuously measuring caustic strength, is technically acceptable.
Subpart FFFF requires that the scrubbers be monitored continuously
either via continuous pH measurement and recording as specified in 40
CFR 63.994(c)(1)(i) and 63.998(a)(2)(ii)(D), or via continuously
monitoring and recording the caustic strength of the effluent. Use of a
continuous pH meter or caustic strength analyzer may be unreliable due
to fouling. The AMP includes frequent grab sampling to monitor caustic
strength based on a worst case loading scenario.
Abstract for [Z120001]
Q: Is an inter-plant pipeline which transports liquids that are at
least 10 percent benzene by weight between two major source facilities,
each belonging to Equistar Chemicals in Alvin, Texas, subject to part
61 NESHAP subparts J and V?
A: Yes. An inter-plant pipeline that transports benzene liquids is
an emission source that is in benzene service according to 40 CFR
61.110 and 61.111, regardless of whether or not the pipeline is defined
as a discrete process unit. 40 CFR 61.110(a) includes valves,
connectors or systems in benzene service, regardless of their location,
and subpart V applies as the leak detection provision for subpart J,
per 40 CFR 61.111.
Abstract for [M120015]
Q: Does EPA approve an alternate work practice for monitoring
hydrogen sulfide (H2S) at bypass lines associated with
sulfur recovery unit (SRU) sulfur pits, which are subject to both MACT
subpart UUU and NSPS subpart J, and the terms of a Consent Decree (CD),
at the Flint Hills Resources Corpus Christi, Texas East and West
refineries?
A: No. EPA does not approve the alternate work practice because it
would be in direct conflict with both the rule and the intent of the
CD, and would result in non-compliance. The SRUs and sulfur pits are
subject to a CD that requires sulfur pit emissions to be continuously
monitored and counted toward SRU total emissions for compliance
demonstration with the NSPS subpart J limit for sulfur dioxide
(SO2). Since the alternative work practice proposed by Flint
Hills did not include continuous monitoring per 40 CFR 60.104(a)(2),
the data necessary to comply with the portion of the CD requiring
aggregation of sulfur pit emissions for compliance demonstration with
the NSPS subpart J SO2 limit would not be collected.
Abstract for [Z140005]
Q: Does EPA approve an exemption from NESHAP subpart WWWWWW under
the definition of research and development for the electroplating and
surface finishing facility at Los Alamos National Laboratory in New
Mexico?
A: Yes. Based on a review of 40 CFR 63.11505(d)(2) and the
definition of a research and development process unit at 40 CFR
63.11511, EPA determines that the facility meets the definition and is
not subject to NESHAP subpart WWWWWW.
Abstract for [M120018]
Q: Will EPA approve Motiva Enterprises' (Motiva) Alternative
Monitoring Plan (AMP) under 40 CFR 60.8 and 60.13(i)(3) for monitoring
wet gas scrubbers (WGS) on a refinery Fluid Catalytic Cracking Unit
(FCCU), in lieu of a Continuous Opacity Monitoring System (COMS), due
to moisture interference on opacity readings in the stack, to
demonstrate compliance with the opacity limit under 40 CFR 60.102(a)(2)
and requirements of MACT subpart UUU at Motiva's Port Arthur, Texas
refinery?
A: Yes. EPA conditionally approves Motiva's AMP. A performance test
is necessary to establish Operating Parameter Limits (OPLs) and other
operating and monitoring conditions required for demonstrating
compliance with NSPS subpart J, MACT subpart UUU and the Consent Decree
for each WGS. The EPA response letter specifies the operating
conditions, operating parameters, test notice deadlines, and
notification content that are conditions of the approval. Interim OPLs
are provided.
Abstract for [M120020]
Q: Does EPA approve the Alternative Monitoring Plan (AMP) for
parametric monitoring on caustic scrubbers used to control hydrochloric
acid emissions from storage tanks, loading, and process vents under 40
CFR part 63 subpart NNNNN at the Rubicon facility in Geismar,
Louisiana?
A: Yes. Based on the information provided in Rubicon's request, EPA
conditionally approves the AMP. A minimum pH operating parameter limit
(OPL), and a minimum recirculating liquid flow rate, pursuant to 40 CFR
63.9020(e)(1)(i), must be established during a performance test
conducted
[[Page 22180]]
under worst case emissions operating scenario. The scrubbers'
effectiveness in meeting subpart NNNNN emission standards during normal
operations will be ensured by continuous monitoring of the two OPLs.
Abstract for [1200038]
Q1: Can equivalency testing be approved to relocate the flue gas
continuous opacity monitoring system (COMS) on the stack outlet of a
wet gas scrubber (WGS) covered under NSPS subpart D at the Texas
Municipal Power Agency (TMPA) Gibbons Creek Electric Steam Generating
Station Unit 1?
A1: Yes. 40 CFR part 60 Appendix B Performance Specification 1 (PS
1) Section 8.1 (2)(i) and (ii) specify measurement location and light
beam path requirements for COMS. If the proposed alternate COMS
locations do not meet these requirements, equivalency testing must be
conducted in accordance with PS 1 Section 8.1 (2)(iii) for each
possible alternative location. Based on the test proposal, EPA approves
the request for conducting preliminary equivalency testing only, with a
60-day notification provided to the State authority.
Q2: What if there are separate ducts that split the vent stream gas
flow?
A2: Relocation and the preliminary equivalency testing must include
the use of two COMS units in order to provide opacity readings
representative of total emissions.
Q3: What must the facility do to obtain subsequent approval for
permanent relocation of the stack COMS?
A3: TMPA must provide the data and operating information from the
preliminary equivalency testing for the alternative location ultimately
selected, in accordance with the applicable performance test reporting
requirements of NSPS subparts A and D. In accordance with PS 1 Section
8.1 (2)(iii), the average opacity value measured at each temporary COMS
at the selected alternate location must be within +/- 10 percent of the
average opacity value measured at the existing flue gas stack COMS, and
the difference between any two average opacity values must be less than
2 percent opacity (absolute value).
Abstract for [M120021]
Q: Does EPA approve a common schedule for submitting periodic
reports under the Hazardous Organic part 63 NESHAP, subparts G and H,
at the Union Carbide Texas City, Texas facility?
A: Yes. EPA approves the common schedule provided the reporting
requirement of 40 CFR 63.152(c)(1) is satisfied, which only allows a
60-day lag between the end of the reporting period and the due date of
a periodic report. EPA reviewed the requirements of 40 CFR 63.10(a)(6)
and 63.9(i), and concurred that the proposed reporting schedule
satisfies the requirements of 40 CFR 63.152(c)(1).
Abstract for [1200039]
Q: Does EPA approve an Alternative Monitoring Plan (AMP) for
monitoring hydrogen sulfide (H2S) for a refinery
hydrocracker feed surge drum off-gas vent stream combusted at four
hydrocracker heaters at the Valero Refining Corpus Christi, Texas West
refinery?
A: Yes. EPA approves Valero's AMP based on the description of the
process vent streams, the design of the vent gas controls, and the
H2S monitoring data furnished. The approval specifies
operating parameter limits for total sulfur and temperature. Valero
must follow the seven step process detailed in the Valero consent
decree appendix on Alternative Monitoring Plans for NSPS subpart J
Refinery Fuel Gas.
Abstract for [1200040]
Q: Does EPA approve an Alternative Monitoring Plan (AMP) for
monitoring hydrogen sulfide (H2S) for a refinery process
feed surge drum off-gas vent stream combusted at a charge heater under
NSPS subpart J at the Valero Refining Corpus Christi, Texas West
refinery?
A: Yes. EPA approves Valero's AMP based on the description of the
process vent stream, the design of the vent gas controls, and the
H2S monitoring data furnished. The approval specifies
operating parameter limits for total sulfur and temperature. Valero
must follow the seven step process detailed in the Valero consent
decree appendix on Alternative Monitoring Plans for NSPS subpart J
Refinery Fuel Gas.
Abstract for [1200041]
Q: Does EPA approve an alternative monitoring request for
monitoring hydrogen sulfide (H2S) the No. 4 vent stream at
the Valero Refining West Plant in Corpus Christi, Texas? The request
involves vent streams from the Oleflex Reactor Lock Hopper Engager off-
gas vent stream combusted at the Oleflex Interheater.
A: Yes. EPA approves Valero's alternative monitoring request based
on the description of the process vent stream, the design of the vent
gas controls, and the H2S monitoring data furnished. There
will be no points where sour gas can be introduced into the vent gas
stream. The effluent is to be sampled and tested daily. Valero must
follow the seven step process (Alternative Monitoring Plans for NSPS
subpart J Refinery Fuel Gas) in the consent decree for the No. 4 vent
stream.
Abstract for [1200042]
Q: Does EPA approve an Alternative Monitoring Plan (AMP) for
monitoring hydrogen sulfide (H2S) of vent gases from the
control of diesel and jet fuel truck loading, toluene and reformate
storage tanks, and groundwater recovery wells at the Valero Refining
Corpus Christi, Texas East refinery? The vent streams are combusted at
the truck rack thermal oxidizer enclosed vapor combustor.
A: Yes. EPA approves Valero's AMP based on the description of the
process vent stream, the design of the vent gas controls, and the
H2S monitoring data furnished. Valero must follow the seven
step process detailed in the Alternative Monitoring Plans for NSPS
subpart J Refinery Fuel Gas appendix of Valero's consent decree. The
approval specifies an H2S operating limit from each of the
emission sources (e.g., loading, tanks, wells) covered by the AMP.
Abstract for [1200046]
Q: Does EPA approve single-point testing in place of Method 1 or 1A
for required testing of engine emissions under 40 CFR part 60 subpart
JJJJ, for the ConocoPhillips Lake Pelto Compressor Barge, located
offshore in southern Louisiana?
A: Yes. EPA approves ConocoPhillips' single-point testing, since
the engines are located over water, and are difficult to test due to
limited space.
Abstract for [1200062]
Q1: Is the installation of a backup vapor recovery unit (BU-VRU) to
capture emissions from a glycol dehydrator unit, which includes a
compressor, at the Marathon Petroleum Indian Basin Gas Plant near
Carlsbad, New Mexico, considered a modification of an affected facility
and thus subject to NSPS subpart KKK?
A1: Based on the information provided by the Air Quality Bureau of
the New Mexico Environment Department (AQB-NMED), EPA determines that
the installation of the BU-VRU compressor at the Indian Basin Gas Plant
is subject to NSPS subpart KKK. The compressor is an affected facility
under NSPS subpart KKK that was constructed after the applicability
date and is presumed to be in VOC or wet gas service. The pollution
control device exemption in 40 CFR 60.14(e) of
[[Page 22181]]
the General Provisions is superseded by 40 CFR 60.630 and therefore
does not apply. In addition, the NSPS subpart KKK does not include
exemptions for compressor emergency operations or operating less than
500 hours per year. With respect to whether the other affected
facility, which includes all other equipment (except compressors), that
are part of the glycol dehydrator process unit, EPA cannot make a
modification determination since there is no information on emission
increases or decreases available.
Q2: Are the two storage tanks at the Indian Basin Gas Plant subject
to NSPS subpart Kb, or are they exempt under the custody transfer
exemption in 40 CFR 60.110b(d)(4)?
A2: Based on the information provided by AQB-NMED, EPA determines
that the storage tanks are subject to NSPS subpart Kb. The Indian Basin
Gas Plant is not part of the producing operation and its tanks are
after the point of custody transfer as defined at 40 CFR 60.111(b).
Therefore, the tanks do not qualify for the ``prior to custody
transfer'' exemption in 40 CFR 60.110b(d)(4).
Abstract for [M120027]
Q1: Does EPA agree with the determinations of the Portsmouth Local
Air Agency and the Southeast District Office of the Ohio EPA that the
America Styrenics Hanging Rock and Marietta, Ohio facilities are
subject to the MACT if they changed processes after the compliance date
such that their potential emissions are well below the HAP major source
thresholds?
A1: Yes. Based on the information provided by the Portsmouth Local
Air Agency, EPA determines that the facilities are still subject to the
major source MACT standard because it is EPA's position that any source
that is a major source of HAP on the first substantive compliance date
of an applicable NESHAP will remain subject to that NESHAP regardless
of the level of the source's subsequent emissions.
Q2: Are these facilities still subject to Title V if their HAP
emissions potential was the only criteria that made them subject to
Title V requirements?
A2: Yes. Because the facilities are subject to a major source MACT
standard, they are also subject to Title V permitting requirements
under Section 502(a) of the CAA, 42 U.S.C. 7661a(a).
Abstract for [M120029]
Q: Does EPA approve an alternative monitoring frequency for
inspections of once per month rather than every 30 days under the Pulp
and Paper MACT for Smurfit-Stone Container Corporation in Coshocton,
Ohio?
A: Yes. EPA approves this minor modification to the monitoring
frequency under 40 CFR 63.8(b)(i) provided that the monitoring events
are at least 21 days apart.
Abstract for [1200087]
Q: Does EPA approve a request to use a subtractive method for the
NOx compliance determination and use of a temporary Continuous Emission
Monitoring System (CEMs) for the initial performance test for a NSPS
subpart Db affected facility at Valero Refining's Ethanol Plant in
Bloomingburg, Ohio? The proposed method uses combined emissions from
this subpart Db facility and another affected facility as determined by
a Continuous Emission Monitoring System (CEMS), and subtracts the
emissions from the other facility as read by a separate CEMS.
A: Yes. EPA approves the subtractive compliance determination
approach under 40 CFR 60.8(b) authority for the initial performance
testing. This request was necessary because, while the NSPS allows for
the location of a CEMS in a stack serving multiple affected sources for
the purpose of demonstration of continuous compliance, no such
allowance is made for the initial performance testing requirement.
Abstract for [Z140004]
Q1: Are emergency engines located at commercial sources that are
used for telecommunications purposes exempt from the Reciprocating
Internal Combustion Engines (RICE) NESHAP regulations at 40 CFR part
63, subpart ZZZZ?
A1: Yes. The requirements at 40 CFR part 63.6590(b)(3) state that
emergency engines located at area sources that are classified as
commercial, institutional or residential emergency stationary RICE are
not subject to the requirements at 40 CFR part 63, subpart ZZZZ.
Q2: Are emergency engines used by telecommunication facilities that
are installed and located on industrial property also exempt?
A2: The applicability of the RICE NESHAP is dependent on whether
the commercial or industrial operation has common control over the
emergency engine. If the industrial facility has control, the engine
could be subject to the RICE NESHAP.
Abstract for [1400016]
Q1: Is Kippur Corporation's (Kippur) dual chamber, commercial
incinerator which thermally destroys contraband for U.S. Customs and
Border Protection in El Paso, Texas subject to regulation as an ``other
solid waste incineration'' (OSWI) unit under 40 CFR part 60 subparts
EEEE and FFFF?
A1: Yes. Based on the information submitted by Kippur, EPA
determines that the contraband incinerator is an OSWI unit subject to
either NSPS subpart EEEE or subpart FFFF. In addition, the incinerator
would not be subject to subpart EEEE because an air pollution abatement
equipment is not considered part of an OSWI unit. Therefore, the
increased feed rate caused by the higher air flow volume resulting from
the addition of a second baghouse on the OSWI unit does not constitute
a modification of the incinerator under NSPS subpart EEEE. Based on
this and additional supplemental information Kippur provided, the OSWI
Unit is therefore subject to NSPS subpart FFFF since subpart EEEE
applicability was not trigger with the OSWI unit changes consistent
with 40 CFR 60.2992.
Q2: Does EPA approve a petition for approval of operating parameter
limits (OPLs) in lieu of installing a wet scrubber to comply with
emission limitations?
A2: No. In a separate September 12, 2012 letter, EPA disapproved
the petition because specific information was lacking for final
approval. Therefore, Kippur must comply with the appropriate NSPS
subpart FFFF requirements.
Abstract for [1400019]
Q1: The Cornerstone Environmental Group, LLC. on behalf of American
Disposal Services of Illinois, which owns the Livingston Landfill,
requests a clarification as to whether the Alternative Compliance
Timeline (ACT) requests are due 15 days after an initial exceedance is
identified through required monitoring activities, pursuant to the
requirements in 40 CFR 60.755(a)(3) and (a)(s).
A1: EPA indicates that 40 CFR 60.755 requires landfill owner/
operators to repair the cause of an exceedance within 15 days, or
expand the gas collection system within 120 days. In the event that the
landfill owner or operator, despite its best efforts, is unable to make
the necessary repairs to resolve the exceedance within 15 days, and it
believes that an expansion of gas collection is unwarranted, the
landfill owner or operator may submit for approval an ACT request for
correcting the as soon as possible (i.e., as soon as it knows that it
will not be able to correct the exceedance in 15 days and it is
unwarranted to expand the gas collection system) to avoid being in
[[Page 22182]]
violation of the rule and communicate the reasons for the exceedance,
results of the investigation, and schedule for corrective action.
Q2: Are ACT requests necessary if the owner/operator chooses to
expand the gas collection system and is unable to complete the
expansion project within 120 days?
A2: Yes. The landfill owner or operator may submit an ACT request
as soon as it determines that it cannot meet the 120 day deadline to
avoid being in violation of the rule. See above response under A1.
Q3: What information is included in an ACT request?
A3: EPA's response describes a number of items that should be
included, at a minimum. The request must promptly identify the problem,
be very detailed, and contain substantial reasons beyond the control of
the facility owner or operator why the exceedances could not and cannot
be completed within the prescribed time frame allowed in the rule.
Q4: If a facility makes repairs to a well to restore the well field
to its original designed capacity, or replaces the well in-kind, does
that constitute an expansion of the gas collection system (thereby
causing the 120-day deadline to be applicable)?
A4: No. An expansion of the gas collection system consists of an
increase beyond the original design capacity.
Abstract for [A140003]
Q1: Are bridges considered regulated structures under the asbestos
NESHAP?
A1: Yes. In a response to the California Air Resource Board, EPA
indicated that a bridge is a structure within the definition of a
facility. As discussed in the October 1990 Background Information
Document for Asbestos, it is prudent not to exclude structures such as
bridges.
Q2: Is a thorough inspection of a bridge for the presence of
asbestos, including Category I and Category II, required under the
asbestos NESHAP?
A2: Yes. Under 40 CFR 61.145(a), a thorough inspection of any
facility is required before demolition or renovation to identify
friable asbestos, Category I and Category II nonfriable asbestos-
containing material (ACM) and Category I and Category II nonfriable ACM
that are not friable at the time of the inspection but will be made
friable due to the demolition or renovation.
Q3: Is bridge concrete Category I, or is it Category II nonfriable
ACM?
A3: Bridge concrete is not listed as Category I nonfriable ACM.
According to 40 CFR 61.141, Bridge concrete is considered Category II
nonfriable ACM if it contains more than 1 percent asbestos that, when
dry, cannot be crumbled, pulverized, or reduced to powder by hand
pressure.
Q4: Must bridge concrete be sampled for the presence of asbestos
before demolition?
A4: The bridge concrete must be thoroughly inspected. See 40 CFR
61.145(a). Sampling is done to determine whether the material is ACM or
not. The amount of ACM that is or will be made friable during the
demolition factors into whether asbestos NESHAP requirements apply.
Q5: If the bridge concrete was never tested for the presence of
asbestos before demolition and now the concrete is going to be crushed
and recycled, must the concrete be tested for asbestos before crushing
and recycling?
A5: The concrete at a demolition operation regulated by 40 CFR
61.145 must be thoroughly inspected before the demolition operation to
determine whether the material is ACM. The recycling could be
considered part of the demolition operation and require the owner/
operator to sample to determine whether the concrete is ACM. The
results will determine whether the concrete can continue to be recycled
or must be managed and disposed of as regulated ACM.
Abstract for [M140006]
Q: Does K&K Ironworks in Chicago, Illinois remain subject to 40 CFR
part 63 subpart MMMM given that they no longer use the quantity of
coatings required by 40 CFR 63.3881(b) for an affected source to be
covered by Subpart MMMM, and they meet the criteria established at 40
CFR 63.3881(c)(1) to be excluded from coverage of subpart MMMM?
A: Although K&K Ironworks of Chicago operations no longer fall
under the types of activities subject to Subpart MMMM, there may be
requirements of subpart MMMM and 40 CFR part 63 subpart A that did not
immediately terminate when the company discontinued the use of coatings
that contain HAPs. For example, the records retention and recordkeeping
requirements at 40 CFR 63.3931(b) and 63.10(b)(3) are continuing
obligations, that were triggered when the company used xylene.
Abstract for [M140008]
Q: Frontier Refining requested an applicability determination
regarding the timing of tank inspections to meet the annual tank
inspection requirements under NESHAP subpart G for the Holly Frontier
facility in Wyoming. Can the annual inspection requirement be
accomplished within an 11-13 month window from the prior inspection?
A: Yes. If a regulation does not specifically state what is meant
by the ``once per'' (timeframe), the EPA interprets the timeframe to
mean at some point within the timeframe and at a reasonable interval
between events. See, for example, 40 CFR 63.100(k)(9)(iii). A once per
month obligation means sometime within the month, but not the last day
of one month and the first day of the next month, because that is not a
reasonable time interval. For annual requirements, a reasonable
interval between events would be between 11 and 13 months.
Abstract for [1400021]
Q: Does EPA agree that Calumet Superior's two steam generating
boilers located at its petroleum refinery in Superior, Wisconsin, and
which are fuel gas combustion devices (FGCDs) affected facilities under
NSPS subpart Ja, do not meet the definition of a process heaters under
NSPS subpart Ja, and therefore are not subject to the emission limits,
performance testing, monitoring and excess emission reporting
requirements for NOx located at 40 CFR 60.102a(g)(2), 60.104a(i),
60.107a(c), 60.107a(d) and 60.102a(i)?
A: Yes. EPA agrees that Calumet Superior's boilers meet the
definition of FGCDs and do not meet the definition of process heaters
under NSPS subpart Ja. Therefore, the boilers are not subject to any
NOx requirements under NSPS subpart Ja. However, to the extent that the
boilers are affected facilities under the Standards of Performance for
Small Industrial-Commercial-Institutional Steam Generating Units, NSPS
subpart Dc, they may be subject to NOx requirements.
Abstract for [M140009]
Q: May Benson Woodworking in Walpole, New Hampshire de-rate its
Caterpillar 3306 Generator Set from its current capacity of greater
than 300 brake horsepower hour (bhp) to less than 300 bhp by cutting
the existing factory governor seal, resetting the loading screws to the
lower output specification, and then resealing the governor with wire
and a dealer specific lead stamp, to comply with the Reciprocating
Internal Combustion Engines (RICE) NESHAP regulations at 40 CFR part
63, subpart ZZZZ?
A: No. The de-rate method proposal is not approvable by EPA. The
proposed method of de-rating the engine is not permanent in nature.
[[Page 22183]]
Abstract for [M140010]
Q: Can the following physical changes to Benson Woodworking's
Walpole, New Hampshire Caterpillar 3306 Generator Set, including:
removal of the current 400 amp circuit breaker and associated frame;
destruction of the 400 amp frame; and, fabrication and installation of
a new frame to hold a smaller 250 amp circuit that would prevent the
engine output from exceeding 299 bhp, result in a de-rating of engine's
capacity to less than 300 bhp?
A: Yes. Based on the physical changes that Benson has proposed, EPA
approves the de-rating of the unit to less than 300 bhp given the
permanent nature of the physical changes to the unit.
Abstract for [M140011]
Q: Does the NSPS for Stationary Compression Ignition Internal
Combustion Engines, subpart IIII apply to an existing marine propulsion
engine manufactured March 22, 1999 (EU ID#4) that the Alaska Village
Electric Cooperative (AVEC) is planning to relocate as a non-stationary
engine at its existing power plant in Emmonak, Alaska?
A: No. The EU ID#4 engine is not subject to NSPS subpart IIII
because it was manufactured prior to April 1, 2006, and commenced
construction prior to July 11, 2005. The conversion of an existing non-
stationary engine to use as an engine at a stationary source is not
``commencement of construction'' that would trigger new source status
under this rule. However, the EU ID#4 existing engine would be subject
to the NESHAP for Stationary Reciprocating Internal Combustion Engines
(RICE), 40 CFR part 63 subpart ZZZZ when it is operated as a stationary
source.
Abstract for [M140012]
Q1: Did a force majeure event, as defined in 40 CFR part 63 subpart
A, occur at the Chena Power Plant in Fairbanks, Alaska?
A1: Yes. EPA determines that on April 28, 2014, a force majeure
event occurred at the Chena Power Plant in Fairbanks, Alaska, when a
mechanical failure of one of the facility's turbine generator rendered
it inoperable.
Q2: Is a 60 day extension of the performance test deadline under
NESHAP subpart JJJJJJ appropriate?
A2: Yes. The turbine generator, which is subject to a testing
deadline, is needed for representative operation of the boiler when the
load from winter district heating is not there to draw steam from the
boiler. In 60 days (November 17, 2014) the load from winter district
heating will be sufficient. Considering the time estimated to repair
the turbine generator, it is reasonable to extend the deadline for the
boiler compliance testing by 60 days.
Abstract for [M140013]
Q: Can EPA provide further guidance on how to conduct tune-ups
under 40 CFR 63.11223(b), which is Condition 4 of the previously EPA
approved one-year compliance deadline extension for the Eielson Air
Force Base's Central Heat and Power Plant in Alaska? The four existing
coal fired boilers subject to the compliance extension are of the
spreader stoker/traveling grate design and do not have burners.
A: Yes. EPA amends the previous approval of the compliance
extension to provide further guidance on Condition 4 of the approval,
as detailed in the EPA response letter. EPA provides guidance on how to
meet the requirements of 40 CFR 63.11223(b) when burners are not
present. Some requirements of 40 CFR 63.11223(b) do not apply, while
others requirements, such as adjusting the air-to-fuel ratio, and
measurement of oxygen and carbon monoxide are still required to be
performed.
Abstract for [M140014]
Q: Does EPA approve a one-year compliance extension to meet the
NESHAP for Area Sources: Industrial, Commercial and Institutional
Boilers, subpart JJJJJJ, for three existing coal-fired boilers (that
operate as back-ups) located at the Brigham Young University in Idaho
(BYU-Idaho)? The coal-fired boilers will be demolished and replaced
with a new energy plant that will be fueled with natural gas.
A: EPA conditionally approves an extension until December 31, 2014,
to operate three coal-fired boilers in their backup capacity without
the installation of controls that would otherwise be required to meet
the NESHAP subpart JJJJJ. The compliance deadline is extended because
BYU-Idaho is constructing a natural gas source of energy generation as
a replacement source of energy to meet requirements of the CAA
standard. The approval is conditional on BYU-Idaho implementing: (1)
interim compliance deadlines for the construction of the natural gas
replacement energy; and (2) tune-ups specified in 40 CFR 63.11214 for
existing coal-fired boilers with a heat input capacity of less than 10
MM BTU/hr that do not meet the definition of limited-use boiler, or an
oxygen trim system that maintains an optimum air-to-fuel ratio.
Abstract for [Z140007]
Q: Which area source NESHAP regulation applies to the operations at
the BASF Corporation Facility in Lancaster, Texas (Lancaster site)? The
NESHAP regulations to evaluate include: NESHAP subpart BBBBBBB
applicable to Chemical Preparations Industry area source category;
NESHAP subpart VVVVVV applicable to the Chemical Manufacturing Source
Category; and NESHAP subpart CCCCCCC applicable to Paints and Allied
Products Manufacturing.
A: EPA finds that the NESHAP subpart BBBBBBB is applicable because
the operations at the Lancaster site are mixing-type processes, which
are typical of the Chemical Preparations Source Category. EPA
understands the Lancaster Site produces architectural coatings,
primarily acrylic latex-based stucco that contains aggregate, primarily
sand. The Lancaster Site mixes latex dispersions produced off-site with
aggregate and other additives to produce acrylic-based stucco.
Abstract for [A140004]
Q: Does EPA agree with the City of Sarasota, Florida that the
demolition of a single-family residential building acquired by the city
is not subject to the asbestos NESHAP subpart M due to the small
residence exemption?
A: Yes. Based on facts presented in the Memorandum of Law from
Sarasota and the definition of facility in the asbestos NESHAP, EPA
determines the building meets the conditions of a small residential
building (a building containing four or fewer dwelling units) and is
not subject to the asbestos NESHAP regulation. The house was not used
for any institutional, commercial, public, or industrial purpose prior
to the demolition. It is not part of an installation, nor part of any
public or private project.
Abstract for [A140005]
Q: Does EPA approve the Transmission Electron Microscopy test
procedure in place of the point counting procedure used to make a
determination of the presence of asbestos in bulk materials, as
required under the asbestos NESHAP?
A: In a response to Masek Consulting Services, EPA indicates that
the current asbestos regulation requires point counting after
evaluating the sample by Polarized Light Microscopy. The owner/operator
may choose to use Transmission Electron Microscopy only after analyzing
the sample by Polarized Light Microscopy and point counting.
[[Page 22184]]
Abstract for [M140016]
Q: Does EPA agree that the Boise DeRidder Mill No. l Bark Boiler in
DeRidder, Louisiana is a biomass hybrid suspension grate boiler under
NESHAP subpart DDDDD?
A: Yes. EPA agrees that the boiler is subject to NESHAP subpart
DDDDD. The Bark Boiler has characteristics that are consistent with the
definition of hybrid suspension grate boiler at 40 CFR 63.7575.
However, natural gas and tire derived fuel are also present as
potential fuels in the boiler. Therefore, the facility must keep
records to demonstrate that the annual average moisture content is at
or above the 40 percent moisture limit, as required in the rule.
Abstract for [1400022]
Q: Does EPA approve the alternative monitoring plan (AMP) for
product vapors from marine vessel loading operations which are
inherently low in sulfur content, and are combusted in the Marine Vapor
Recovery (MVR) Flare No.3, under NSPS 40 CFR 60 subpart J for the
Chalmette Refining's Chalmette, Louisiana refinery?
A: EPA determines that the AMP is no longer necessary since the
definition of fuel gas has been modified under the September 12, 2012
amendment to subpart J (77 Federal Register 56463). The marine vessel
loading vapor stream does not meet the definition of a fuel gas, as
defined at 40 CFR 60.101(d). Therefore, MVR Flare No.3 does not need to
meet the continuous monitoring requirements of either 40 CFR
60.105(a)(3) or 60.105(a)(4).
Abstract for [1400023]
Q: Can an exemption from monitoring be approved for a fuel gas
stream that is low in sulfur content under NSPS subpart J, for the off-
gas vent stream from the Gasoline Desulfurization Unit Selective
Hydrogenation Unit Surge Drum Vent that is routed to the North Flare at
the Marathon Oil facility in Garyville, Louisiana?
A: Yes. Based on Marathon's description of the process vent
streams, the design of the vent gas controls, and the H2S
monitoring data furnished, EPA conditionally approves the exemption.
EPA finds that, when controlled as delineated in the response letter,
the vent gas stream combusted is inherently low in sulfur, according to
40 CFR 60.105(a)(4)(iv)(D), and does not need to meet the continuous
monitoring requirements of 40 CFR 60.105(a)(3) or 60.105(a)(4). EPA
included the facility's proposed operating parameter limits, which the
facility must continue to monitor, as part of the conditional approval.
Abstract for [1400024]
Q: Can an exemption in lieu of Alternative Monitoring Plan be
approved for a fuel gas stream that is low in sulfur under NSPS 40 CFR
60 subpart J at the ExxonMobil refinery in Baytown, Texas? The refinery
proposes to combust commercial grade natural gas as a supplemental
fuel, in combination with refinery fuel gas vent streams.
A: Yes. Based on ExxonMobil's description of the process vent
streams, the design of the vent gas controls, and the H2S
monitoring data furnished, EPA conditionally approves the exemption.
EPA finds that the mixture of non-monitored commercial natural gas and
refinery fuel vent gas stream combusted is inherently low in sulfur,
according to 40 CFR 60.105(a)(4)(iv)(D), when used and controlled as
described in the EPA response letter. EPA included the facility's
proposed operating parameter limits, which the facility must continue
to monitor, as part of the conditional approval. Therefore, the fuel
gas combustion devices listed in the request do not need to meet the
continuous monitoring requirements of 40 CFR 60.105(a)(3) or
60.105(a)(4).
Abstract for [1400025]
Q: Is the propane refrigeration system used at the Enbridge Nine
Mile Gas Plant in Dewey County, Oklahoma subject to the requirements of
NSPS 40 CFR 60 subpart KKK?
A: Yes. EPA determines that propane system is subject to NSPS KKK
based upon the information the company provided. The propane
refrigeration system is a process unit that can also operate
independently if supplied with sufficient feed. The propane
refrigeration system is ``equipment'' under 40 CFR 60.631 because it
consists of valves, connectors, and compressors in VOC service. These
components are in light liquid VOC service because they contain or
contact propane, which constitutes at least 97 percent by weight of
content of the refrigeration system, and the propane is a liquid within
the operating conditions of the refrigeration system.
Abstract for [1400026]
Q: Are two natural gas reciprocating compressors which were
transferred from a ``laydown'' yard to the Fayetteville Gathering
Hattieville Compressor Station, located in Hattieville, Arkansas,
affected facilities subject to the requirements of NSPS subpart OOOO?
A: No. Relocation, by itself, does not trigger NSPS applicability
through modification. Based upon the fact that the company commenced
construction of the two compressors on a continuous basis prior to the
effective date of NSPS subpart OOOO, nor were they modified, these
units are not affected facilities under the subpart. EPA clarified in
final rule preamble to NSPS OOOO that relocation does not subject a
source to new source standards. Additionally, the General Provisions to
Part 60 contain similar language, that relocation or change in
ownership, by itself, is not a modification.
Abstract for [1400027]
Q1: Does EPA provide final approval of an Alternative Monitoring
Plan (AMP) for parametric monitoring in lieu of a continuous opacity
monitor for a Wet Gas Scrubber (WGS) on a Fluidized Catalytic Cracking
Unit (FCCU) at Holly Refining & Marketing in Tulsa, Oklahoma (Holly)
under NSPS 40 CFR 60, subpart J, and NESHAP 40 CFR 63, subpart UUU,
based on submittal of test results?
A1: Yes. EPA grants final approval of Holly's AMP request. Holly
conducted a performance test and submitted additional data pertaining
to a prior, conditionally approved AMP. EPA reviewed the performance
test results and found the data supportive for establishing final OPLs
for the WGS, which included minimum Liquid-to-Gas Ratios, based on 3-
hour, hourly rolling averages, for operation of the WGS with one or two
nozzles.
Abstract for [1400028]
Q: May the Ineos Chocolate Bayou facility in Alvin, Texas, which is
subject to both 40 CFR part 60, Standards of Performance for Volatile
Organic Compound (VOC) Emissions from Synthetic Organic Chemical
Manufacturing Industry (SOCMI) Distillation Operations (NSPS subpart
NNN) and Reactor Processes (NSPS subpart RRR) use the monitoring and
testing provisions in NSPS subpart RRR in lieu of NSPS subpart NNN for
the process heaters?
A: Yes. EPA approves the request for meeting Subpart RRR in lieu of
NSPS subpart NNN requirements for testing, monitoring, and
recordkeeping for use of process heaters as control devices for
compliance with the standards of both subparts. This would require
monitoring of small vent and drain valves utilized for maintenance
events during maintenance in accordance with NSPS subpart RRR since
they act as bypass valves. In addition, the schematic required by 40
CFR 60.705(s) is required with the initial report and must be
maintained on site to ensure that the
[[Page 22185]]
affected vent streams are being routed to appropriate control devices
without bypass.
Abstract for [1400029]
Q1: Does EPA agree with Kinder Morgan that the Condensate Splitter
Flare located at the Galena Park Condensate Processing Facility in
Harris County, Texas is subject to NSPS subpart Ja?
A1: No. EPA is unable to verify applicability of NSPS subpart Ja
because sufficient information about the facility or the operations and
processes vented to the flare were not provided.
Q2: Does EPA approve an Alternative Monitoring Plan (AMP) request
for the Condensate Splitter Flare?
A2: No. Kinder Morgan did not furnish sufficient detail about vent
streams routed to the flare, or adequately describe the specific
refinery process that would produce low sulfur content vent streams.
Assuming the vent streams are fuel gas streams subject to NSPS subpart
Ja, we cannot approve any AMP that seeks to circumvent a specific
emissions monitoring requirement for affected facility operations.
Under NSPS, new facilities must be constructed in such a manner that
monitors are installed to demonstrate initial compliance and ensure
ongoing compliance until such time that an exemption can be met.
Furthermore, applications for exemptions to a rule must provide
sufficient data at the time of the request in order to be evaluated for
approval.
Abstract for [1400030]
Q1: Does EPA approve the HollyFrontier Companies' request for
approval of an Alternative Monitoring Plan (AMP) for monitoring oxygen
in the stack, in lieu of parametric monitoring to substitute for a
Continuous Emissions Monitoring System, for the hydrocracker reboiler
at Navajo Refining's Artesia, New Mexico refinery (Navajo), to comply
with the NOX and oxygen standards in NSPS, 40 CFR part 60
subpart Ja?
A1: Yes. EPA determines that Navajo's AMP that combines monitoring
oxygen in the stack along with other specific process monitoring
parameters is acceptable based on the limited usage of refinery fuel
gas and the information submitted, including the performance test
results. Navajo sampled the fuel gas at the reboiler to demonstrate
that the stream is 100 percent purchased natural gas. Also, to improve
the efficiency of the heater, Navajo installed new burner tips to
better combust the purchased natural gas. As a result, NOX
and O2 emissions were reduced, as verified by a performance
test.
Abstract for [1400031]
Q: Does EPA approve an Alternative Monitoring Plan (AMP) for PSC
Industrial to conduct monitoring of H2S emissions at various
locations in EPA Region 6, in lieu of installing a continuous emission
monitoring system (CEMS), when performing tank degassing and other
similar operations controlled by portable, temporary thermal oxidizers,
at refineries that are subject to NSPS 40 CFR 60 subparts J or Ja?
A: Yes. EPA conditionally approves PSC Industrial's AMP request.
Based on the description of the process, the vent gas streams, the
design of the vent gas controls, and the H2S monitoring data
furnished, EPA finds that it is impractical to require monitoring via
an H2S CEMS as specified by NSPS subparts J and Ja for the specific
portable and temporary combustion device use. EPA included operating
parameter limits (OPLs) and data which the refineries must furnish as
part of the conditional approval. This conditional approval applies to
this company's refineries in EPA Region 6 only. EPA's conditional
approval should also be referenced and appropriately incorporated into
PSC Industrial's new source review permit in each state where degassing
operations at refineries will occur, to ensure federal enforceability.
Abstract for [1400032]
Q: Can Samson Exploration, Houston, Texas submit hard copy
photographs with the required GIS and date stamp data printed below
each photograph in streamlined annual reports required under 40 CFR
60.5420(b)(2) of NSPS subpart OOOO?
A: Yes. The inclusion of such types of submissions in annual
reports is acceptable. There is no regulatory prohibition against
submitting hard copies which have the date and GIS coordinates printed
beneath each photograph, provided that the proximity of each photograph
and its associated data ensures clear correlation. EPA further
clarified that, in conjunction with the self-certification statement
required under 40 CFR 60.5420(b)(1)(iv), a statement should be included
that digital images of the photographs for each well completion are
retained, such that the digital image files contain embedded date
stamps and geographic coordinate stamps to link the photographs with
the specific well completion operations.
Abstract for [1400033]
Q: Can EPA approve an Alternative Monitoring Plan (AMP) for Tristar
Global Energy Solutions Company (Tristar) to conduct monitoring of
hydrogen sulfide (H2S) emissions, in lieu of installing a
continuous emission monitoring system, when performing tank degassing
and other similar operations controlled by portable, temporary thermal
oxidizers, at refineries at various locations that are subject to NSPS
subparts J or Ja?
A: Yes. Based on the description of the process, the vent gas
streams, the design of the vent gas controls, and the H2S
monitoring data furnished, EPA conditionally approves the AMP request.
EPA included operating parameter limits and data which the refineries
must furnish as part of the conditional approval. This conditional
approval applies to Tristar's degreasing operations at refineries in
EPA Region 6 only.
Abstract for [1400034]
Q1: Does EPA agree with Western Farmers Electric Cooperative (WFEC)
that excess emission for the Hugo Generating Station, Choctaw County,
Oklahoma coal-fired boiler, an ``affected facility'' under NSPS for
Fossil Fuel Fired Steam Generators, subpart D, would only be reported
for certain periods of operational status such as when the boiler is
firing fuel for the purpose of generating electricity?
A1: No. EPA disagreed that reporting of excess emissions should be
limited to certain periods of boiler operational status. EPA reiterated
that the NSPS requires reporting of all periods of excess emissions,
including those temporary occurrences that may result in a particular
emission standard being exceeded. Required recordkeeping and reporting
should be viewed, along with O&M and SSM protocols, as a company's
substantiation of acting in good faith to demonstrate compliance with
emission limitations, standards, and work practice standards at all
times. EPA believes that WFEC has misinterpreted certain monitoring,
recordkeeping and reporting provisions in the NSPS and MACT standards
that a combustion source must meet for continuous compliance
demonstration, which we explained in the Regulatory Interpretation
enclosure of the EPA response.
Abstract for [1400035]
Q: Does EPA approve the alternative monitoring Operating Parameter
Limits (OPLs) under NSPS subpart Ec, for a pollution control system on
a new
[[Page 22186]]
medical waste incinerator which consists of a wet gas scrubber (WGS)
followed by a carbon adsorber and cartridge filter, located at the
University of Texas Medical Branch (UTMBG) in Galveston, Texas?
A: Yes. EPA conditionally approves Hydro-Environmental Technologies
petition on behalf UTMBG for an AMP. As part of the conditional
approval, performance testing must be conducted to demonstrate
compliance and establish OPL values for the WGS, carbon adsorber and
cartridge filter. Final approval of the AMP will be based on the OPLs
established and other provisions that may be deemed necessary from our
evaluation of the test results.
Abstract for [1400036]
Q: Will EPA approve the Fuel Analysis Plan for monitoring total
sulfur content of fuels in lieu of SO2 emissions monitoring
under NSPS subpart Db for Industrial-Commercial Institutional Steam
Generating Units for which construction, reconstruction, or
modification commenced after June 19, 1984, at the No. 6 Power Boiler
in Westvaco, Texas L.P. facility (Westvaco)?
A: Yes. EPA conditionally approves Westvaco's Fuel Analysis Plan,
as delineated within the response letter. 40 CFR 60.45b(k) allows
compliance to be demonstrated by a fuel based compliance alternative.
The plan ensures that data will be collected to demonstrate that the
average percentage sulfur concentration in the wood fuel, plus three
standard deviations, will not result in a combined fuel mixture that
will exceed the sulfur emission limit. Westvaco will continue to obtain
and maintain fuel receipts for the other combusted fuels.
Abstract for [1400037]
Q: Can an exemption from monitoring be approved for a fuel gas
stream that is low in sulfur content, under NSPS subpart J, for the
off-gas vent stream from the Merox Off-gas Knockout Pot in the Alky
Stripper Reboiler Heater, at the Valero Refining Meraux facility in
Meraux, Louisiana?
A: Yes. Based on the description of the process vent streams, the
design of the vent gas controls, and the H2S monitoring data
furnished, EPA conditionally approves the exemption in light of changes
made to NSPS subpart J on June 24, 2008 (73 Federal Register 35866).
EPA finds that, when used and controlled as described in the response
letter, the vent gas stream combusted is inherently low in sulfur
according to 40 CFR 60.105(a)(4)(iv)(D) and therefore, the fuel gas
combustion device does not need to meet the continuous monitoring
requirements of 40 CFR 60.105(a)(3) or 60.105(a)(4) for the Merox Off-
gas Knockout Pot fuel gas stream. Valero Meraux is required to monitor
and control the relevant process parameters, as summarized in the
Enclosure, as a condition of this exemption approval.
Abstract for [1100017]
Q: Can alternative monitoring be approved in lieu of a Continuous
Opacity Monitoring System (COMS) since the moisture in the Fluid
Catalytic Cracking Unit exhaust from the wet gas scrubber (WGS) will
interfere with the ability of the COMS to take accurate opacity
readings due to water interference for the Conoco Phillips Sweeny,
Texas Refinery?
A: Yes. EPA approves the alternative monitoring based on
information provided by Conoco, including a stack test report and three
proposed operating parameters limits (OPLs) for the wet gas scrubber.
The OPLs address nozzle pressure, pressure drop, and liquid to gas
ratio.
Dated: April 13, 2015.
Lisa Lund,
Director, Office of Compliance.
[FR Doc. 2015-09242 Filed 4-20-15; 8:45 am]
BILLING CODE 6560-50-P