Recent Posting to the Applicability Determination Index (ADI) Database System of Agency Applicability Determinations, Alternative Monitoring Decisions, and Regulatory Interpretations Pertaining to Standards Under the Clean Air Act, 36121-36129 [2011-15416]
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Federal Register / Vol. 76, No. 119 / Tuesday, June 21, 2011 / Notices
Accessibility: For information on
access or services for individuals with
disabilities, please contact Mr. Aaron
Yeow at (202) 564–2050 or
yeow.aaron@epa.gov. To request
accommodation of a disability, please
contact Mr. Yeow preferably at least ten
days prior to the teleconference to give
EPA as much time as possible to process
your request.
by phone at: (202) 564–7027, or by email at: malave.maria@epa.gov. For
technical questions about the 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:
Dated: June 14, 2011.
Anthony F. Maciorowski,
Deputy Director, EPA Science Advisory Staff
Office.
Background
[FR Doc. 2011–15414 Filed 6–20–11; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
[FRL–9321–1]
Recent Posting to the Applicability
Determination Index (ADI) Database
System of Agency Applicability
Determinations, Alternative Monitoring
Decisions, and Regulatory
Interpretations Pertaining to Standards
Under the Clean Air Act
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 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 Office of Enforcement and
Compliance Assurance (OECA) Web site
at: https://www.epa.gov/compliance/
monitoring/programs/caa/adi.html. The
document 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
wwoods2 on DSK1DXX6B1PROD with NOTICES_PART 1
SUMMARY:
The General Provisions to the NSPS
in 40 Code of Federal Regulations (CFR)
Part 60 and the General Provisions to
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
[which includes Maximum Achievable
Control Technology (MACT) standards]
and section 111(d) of the Clean Air Act
(CAA) regulations contain no specific
regulatory provision that sources may
request applicability determinations,
EPA responds to written inquiries
regarding applicability for the part 63
and section 111(d) programs as well.
The NSPS and NESHAP also allow
sources to seek permission to use
monitoring or recordkeeping that are
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 on the
ADI on a quarterly basis. 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. The
letters and memoranda may be searched
by date, office of issuance, subpart,
citation, control number, or by string
word searches.
Today’s notice comprises a summary
of 47 such documents added to the ADI
on May 25, 2011. The subject and
header of each letter and memorandum
are listed in this notice, 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: https://
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 May 25, 2011; the applicable
category; the subpart(s) of 40 CFR part
60, 61, or 63 (as applicable) covered by
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 section
307(b)(1) of the Clean Air Act. For
example, this notice does not make an
applicability determination for a
particular source into a nationwide rule.
Neither does it purport to make any
document that was previously nonbinding into a binding document.
ADI DETERMINATIONS UPLOADED ON APRIL X, 2011
Control number
Categories
Subparts
M090044 ............................................
1000001 .............................................
1000002 .............................................
MACT ..........
NSPS ..........
MACT,
NSPS.
NSPS ..........
MACT ..........
MACT ..........
A, RRR ........
VVV .............
AAAA,
WWW.
WWW ..........
EEEE ..........
MMMM ........
1000003 .............................................
M100001 ............................................
M100002 ............................................
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Title
Alternate Operating Scenarios for Production Furnace
Installation of a Pigment Mixing and Milling Process
Gas Treatment System Used for Energy Recovery Purposes
Monitoring Lids of Gas Well Sumps as ‘Surface’ of the Landfill
Once In Always In Policy
Use of Non-Regenerative Carbon Adsorption System
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36121
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ADI DETERMINATIONS UPLOADED ON APRIL X, 2011—Continued
Control number
Categories
Subparts
Title
Alternative Control Device Operating Parameters
Solid State Polymerization PET Process
Excess Emissions Reporting for a Waste Liquid Fuel-Fired Boiler
Boiler Modification
Alternative Monitoring
Landfill Gas Treatment System
Secondary Carbon Adsorption Requirements for Resold Equipment
Landfill Gas Operating Temperatures
Minimum Secondary Combustion Chamber Temperature Operating Parameter Limit
Thermal Destruction Unit Determination
Relocation of Facility and Reduction of Emissions after NESHAP Compliance Date
Alternative Method for Fuel Supplier Certification
Use of Method 7E at Nitric Acid Plants and Method 6C at Sulfuric Acid
Plants
Commence Construction for Gas Turbine
Commence Construction for Gas Turbine
Installation of a Capacitor Bank and Tuned Reactor
Conversion of Post-Sorted Municipal Solid Waste Feedstock
Alternative Monitoring Plan
Alternative Monitoring Plan
Modification of Alternative Monitoring Plan
Modification of Alternative Monitoring Plan
Alternative Monitoring of Hydrochloric Acid (HCl) Bubbler Control Device
External Floating Roof Tank Enclosed with Fixed Roof
Amended Design Capacity Reports
Removal of Asbestos Containing Coating Materials from Stator Bars
Cold Core Machines Used for Capture and Wet Acid Scrubbers
Installation of Combustion Turbines and Direct-Fired Heaters
Mining of Naturally Occurring Oil Sands and Extraction of Bitumen
Alternative Monitoring Plan
Alternative Monitoring Plan
Comprehensive Performance Test Plan
Alternative Monitoring Plan
M100004 ............................................
M100005 ............................................
M100006 ............................................
1000004 .............................................
1000007 .............................................
1000008 .............................................
M100009 ............................................
1000009 .............................................
M100010 ............................................
MACT
MACT
MACT
NSPS
NSPS
NSPS
MACT
NSPS
MACT
..........
..........
..........
..........
..........
..........
..........
..........
..........
NNNNN .......
FFFF, JJJ ....
EEE .............
A, Db ...........
Y ..................
WWW ..........
M .................
WWW ..........
EEE .............
1000011 .............................................
M100012 ............................................
NSPS ..........
MACT ..........
CCCC ..........
JJ ................
1000012 .............................................
1000013 .............................................
NSPS ..........
NSPS ..........
Dc, IIII ..........
G, H .............
1000015 .............................................
1000016 .............................................
1000017 .............................................
1000019 .............................................
M100014 ............................................
M100015 ............................................
M100016 ............................................
M100017 ............................................
M100018 ............................................
1000021 .............................................
1000022 .............................................
A100001 ............................................
M100019 ............................................
1000023 .............................................
1000024 .............................................
M100020 ............................................
M100021 ............................................
M100022 ............................................
1000025 .............................................
NSPS ..........
NSPS ..........
NSPS ..........
NSPS ..........
MACT ..........
MACT ..........
MACT ..........
MACT ..........
MACT ..........
NSPS ..........
NSPS ..........
Asbestos .....
MACT ..........
NSPS ..........
NSPS ..........
MACT ..........
MACT ..........
MACT ..........
NSPS ..........
M100023 ............................................
M100024 ............................................
1000026 .............................................
Z100001 ............................................
M100025 ............................................
M100026 ............................................
M100027 ............................................
M100028 ............................................
A110001 ............................................
MACT ..........
MACT ..........
NSPS ..........
NESHAP .....
MACT ..........
MACT ..........
MACT ..........
MACT ..........
NESHAP .....
KKKK ...........
GG, KKKK ...
A, AAa .........
AAAA ...........
R .................
EEE .............
EEE .............
EEE .............
GGG ............
Kb ................
WWW ..........
M .................
EEEEE ........
KKKK ...........
Ja ................
EEE .............
RRR ............
EEE .............
A, NNN,
RRR.
PPPPP ........
RRR ............
Kb ................
FF ................
EEE .............
EEE .............
EEE .............
EEE .............
M .................
wwoods2 on DSK1DXX6B1PROD with NOTICES_PART 1
Abstracts
Abstract for [M090044]
Q1: Does 40 CFR part 63, subpart
RRR, allow Kaiser Aluminum
Fabricated Products, Inc., the owner/
operator of a secondary aluminum
production furnace, to switch back and
forth between group 1 and group 2
furnace operation at a regular or even
infrequent basis, depending on what its
being fed to the furnace at any given
time, and turn the control device on and
off depending on the operating
scenario?
A1: No. MACT subpart RRR does not
allow for the furnace to be designated
group 1 and 2 at the same time,
depending on what it’s being feed to the
furnace. However, the owner/operator
may choose to re-designate a furnace on
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Appropriate Method for Calculating Reconstruction
Startup, Shutdown, Malfunction Reporting Requirements
Alternative Monitoring Plan
Sour Water Streams Regulation
Alternative Operating Parameters
Modification of Alternative Monitoring Plan
Alternative Monitoring Plan
Modification of Alternative Monitoring Plan
Asbestos NESHAP: Municipalities demolishing and renovating multiple
residential structures as part of an ‘‘urban renewal’’ project.
a very infrequent basis along with a
permit modification.
Q2: Does 40 CFR part 63, subpart
RRR, allow an owner/operator to
operate the furnace as a group 1 furnace,
accepting an undefined mix of clean
and purchased scrap and a fluxing
agent, with the baghouse not operating?
A2: No. A group 1 furnace cannot be
authorized to operate under more than
one set of operating parameters
depending on what is being fed to the
furnace at any given time and the use of
a control device or not. MACT subpart
RRR addresses a single worst-case
scenario when conducting a
performance test to establish operating
parameters, and does not address
alternate operating scenarios.
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Abstract for [1000001]
Q1: Are two mixing vessels and two
milling machines being installed at the
Majilite facility in Dracut,
Massachusetts, considered coating mix
preparation equipment under 40 CFR
part 60, subpart VVV?
A1: Because Majilite’s mixing vessels
will be blending solvent with other
materials to prepare pigments that are
used to prepare polymeric coatings, the
pigment mixing vessels are coating mix
preparation equipment subject to NSPS
subpart VVV. The milling machines,
however, do not fit within the rule
definition of coating mix preparation
equipment.
Q2: Majilite operates one coating line
subject to NSPS, subpart VVV, and that
this coating line and coating mix
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operation use more than 130 Mg of VOC
per year. What are the requirements
under 40 CFR part 60, subpart VVV, for
the coating mix preparation equipment
if the pigment mixing vessels are being
installed without concurrent
construction of a control device?
A2: EPA has determined that because
Majilite’s subpart VVV coating
operation and associated coating mix
preparation equipment use at least 130
Mg of VOC per 12-month period and the
pigment mixing vessels are being
installed without concurrent
construction of a control device, Majilite
must meet the requirements of
60.742(c)(2) for its pigment mixing
vessels, among other requirements.
wwoods2 on DSK1DXX6B1PROD with NOTICES_PART 1
Abstract for [1000002]
Q: Do the processes which occur in
the preliminary treatment system at
Waste Management of New Hampshire’s
(WMNH) Turnkey Recycling and
Environmental Enterprise (TREE)
facility in Rochester, New Hampshire,
meet the requirements for a ‘‘treatment
system’’ under 40 CFR
60.752(b)(2)(iii)(C)?
A: Yes. EPA has determined that the
preliminary treatment system located at
WMNH in which the gas has been
compressed, dewatered, and filtered
down to 10 microns meets the criteria
of a treatment system under 40 CFR
60.752(b)(2)(iii)(C), and is not subject to
the monitoring and recordkeeping
requirements of 40 CFR 60.756(b) and
40 CFR 60.758(b) and (c).
Abstract for [1000003]
Q: Does EPA approve the request of
Allied Imperial Landfill in Imperial,
Pennsylvania to monitor some landfill
gas well sump structure lids as though
they were the ‘‘surface’’ of the landfill,
in accordance with 40 CFR part 60,
subpart WWW?
A: Yes. EPA finds that monitoring the
sump lids is adequate to fulfill the
requirements of NSPS subpart WWWW
based on the intent of NSPS subpart
WWW and the sump structure
construction. Monitoring inside the
sump structure could create an
artificially elevated value for the landfill
gas well(s). If a landfill gas extraction
well (LGFW) monitoring event indicates
readings above 500 ppm around the
circumference of the fiberglass
structure, and/or lid of the structure,
then corrective actions must be
completed, as required by NSPS subpart
WWW.
Abstract for [M100001]
Q: The Pactiv facility located in
Winchester, Virginia, must comply with
40 CFR part 63, subpart EEEE, the
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organic liquid distribution (OLD)
MACT, due to a hazardous air pollutant
(HAP) in a foaming agent used at the
facility. Were the facility to switch the
foaming agent to one that uses less than
5 percent HAPS would the OLD MACT
apply?
A: Yes. The new foaming agent still
contains HAPs, and according to the
‘‘Once in Always In’’ Policy, the OLD
MACT still applies.
Abstract for [M100002]
Q: Does EPA approve the use of a
non-regenerative carbon adsorption
system as the control technology under
40 CFR part 63, subpart MMMM, for the
metal parts coating operations of East
Penn Manufacturing in Lyon Station,
Pennsylvania?
A: Yes. EPA approves this request
based on the conditions set forth in this
letter, and provided that the request
does not relieve East Penn of any other
requirements of MACT subpart MMMM.
Abstract for [M100004]
Q: Does EPA approve alternative
operating parameters under 40 CFR part
63, subpart NNNNN, for the Irgafos V–
47 caustic scrubber at the Ciba
Corporation facility in McIntosh,
Alabama?
A: No. EPA cannot approve the
requested alternatives without
evaluating the performance test data
that is collected using these proposed
alternative parameters which needs to
be submitted by Ciba Corporation to
demonstrate compliance with the
applicable emission limit set out in
Table 1 of MACT subpart NNNNN.
Abstract for [M100005]
Q: Is the polyethylene terephthalate
(PET) solid state polymerization (SSP)
process at the DAK Americas facility in
Cooper River, South Carolina, subject to
40 CFR part 63, subpart FFFF?
A: Yes. The SSP process is a
miscellaneous organic chemical
manufacturing process unit (MCPU)
which manufactures a product, PET,
which is described by the North
American Industry Classification
System 325. In doing so, it, generates a
hazardous air pollutant (HAP),
acetaldehyde. The MCPU is located at a
major source of HAP. Thus, the SSP
process satisfies all of the conditions for
applicability under MACT subpart
FFFF, specifically 40 CFR 63.2435 (a)
and (b)(1) through (3).
Abstract for [M100006]
Q: Does EPA waive excess emissions
reporting requirements under 40 CFR
part 63, subpart EEE, for a waste liquid
fuel-fired boiler system (WFBS) at the
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36123
Diversified Scientific Services facility in
Kingston, Tennessee, if the unit is
equipped with an automatic fuel cutoff?
A: No. EPA does not waive the excess
emissions reporting requirements of
MACT subpart EEE even when the
WFBS has safe guards that minimizes
emissions because there remain
numerous reportable situations
involving continuous monitoring system
devices, such as opacity monitors,
thermocouples, pressure transducers,
and flow meters, that could malfunction
and that should be included in the
required report.
Abstract for [1000004]
Q1: Is the exemption in section
60.14(e)(4) of the General Provisions
applicable to Power Boiler No. 6, at
Rayonier Performance Fibers, in
Fernandina Beach, Florida, even though
the emission rate of nitrogen oxide
(NOX) will increase, such that it will
cause the boiler to not become subject
to NSPS subpart Db, Standards of
Performance for Industrial-CommercialInstitutional Steam Generating?
A1: Yes. Even though there will be an
increase in the NOX emission rate, the
operational or physical changes made at
the facility are not considered
modifications under 40 CFR 60.14(e) of
the General Provisions. Thus, the
changes did not subject the Power
Boiler No. 6 to NSPS subpart Db.
Q2: An interpretation of the reference
in 40 CFR 60.14(e)(4) to the ‘‘facility’s
construction specifications’’ is
requested for Power Boiler No. 6. The
boiler was purchased by Rayonier as a
traveling grate boiler and was later
converted to a bubbling fluidized bed
boiler.
A2: The exemption in 40 CFR
60.14(e)(4) relates to the construction
specifications prior to the date a
standard becomes applicable to a source
category. Because the applicability date
for 40 CFR part 60, subpart Db, is June
18, 1984, 40 CFR 60.14(e)(4) relates to
the construction specifications for
Power Boiler No. 6 prior to that date.
Abstract for [1000007]
Q: Does EPA grant the request of
Detroit Edison’s River Rouge Power
Plant in River Rouge, Michigan, to
eliminate the requirement for
temperature monitors on the gas stream
exits of the thermal dryers?
A. No. Continuous temperature
monitoring, as required in 40 CFR
60.256(a) (1), indicates compliance
status with respect to the carbon
monoxide (CO) limits. The temperature
record ensures the source temperature
correlates with the results of
performance tests or other emissions
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tests. Monitoring temperature is
essential because improperly tuned
operations at off-design levels decrease
combustion efficiency resulting in
increased CO emissions. Additionally,
Detroit Edison has not requested an
alternative form of monitoring (see 60
CFR 60.13(i)), but rather the elimination
of the monitoring requirements. EPA is
unable to grant this request because the
Region does not have authority to
amend NSPS subpart Y.
Abstract for [1000008]
Q: Does the landfill gas treatment
system proposed by the City of Midland,
Michigan, meet the requirements that
allow the landfill gas to be exempt from
control requirements per 40 CFR
60.752(b)(2)(iii)(C) when burned in
internal combustion engines? A: Yes.
Because the proposed landfill gas
treatment system will use 10-micron
filtration and sufficient dewatering, it
meets the current requirements used by
EPA for gas ‘‘treatment’’ and is therefore
exempt from the requirements of 40 CFR
60.752(b)(2)(iii)(C).
Abstract for [M100009]
Q: Is dry cleaning equipment that was
initially installed prior to December 21,
2005, but was removed from its original
location, sold to a new owner, and
relocated subsequent to December 21,
2005, subject to the area source, nonresidential carbon adsorption
requirements at 40 CFR 63.322(o)(2)?
A: Yes. Reselling and relocating dry
cleaning equipment constitutes
installation of a dry cleaning system.
Therefore dry cleaning equipment that
is resold and relocated would be subject
to the secondary carbon adsorption
requirements of 40 CFR 63.322(o)(2).
wwoods2 on DSK1DXX6B1PROD with NOTICES_PART 1
Abstract for [1000009]
Q: Does EPA approve higher landfill
gas temperatures under 40 CFR
60.753(c) for specific extraction and
leachate wells at Veolia’s Glacier Ridge
Landfill near Horicon, Wisconsin?
A: Yes. Because the proposed
operating limit of 148 degrees
Fahrenheit is properly supported by
data that shows there would be a
minimal risk of a landfill fire or
significantly inhibited anaerobic
decomposition, EPA approves the
higher landfill gas temperatures under
40 CFR 60.753(c).
Abstract for [M100010]
Q: Does EPA approve a request to
waive the minimum secondary
combustion chamber temperature
operating parameter limit under 40 CFR
part 63, subpart EEE, for the Heritage-
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WTI (WTI) facility in East Liverpool,
Ohio?
A: No. EPA concludes that the rotary
kiln and the secondary combustion
chamber (SCC) are separate combustion
chambers and thus does not approve the
request under MACT subpart EEE. WTI
cannot legitimately argue that the SCC
at its facility does not contain a steadystate, or near steady-state, process
wherein fuel, hazardous waste, and
oxidizer (i.e., pure oxygen or ambient
air) feed rates are controlled, since the
SCC is engineered to allow WTI to feed
pure oxygen or ambient air into the SCC
to improve combustion. EPA concludes
that the SCC is an area in which
controlled flame combustion of
hazardous waste occurs. Therefore, EPA
disapproves WTI’s request in its original
and revised comprehensive performance
test plans to determine that the Rotary
Kiln and the SCC are one combustion
chamber and to eliminate the need for
a minimum combustion chamber
temperature operating parameter limit.
Abstract for [1000011]
Q: Does 40 CFR part 60, subpart
CCCC, apply to the thermal destruction
unit operated by PIKA International in
Calhoun County, Arkansas?
A: Yes. NSPS subpart CCCC applies
because the waste that is burned (1) Is
a RCRA solid waste, but not a RCRA
hazardous waste; (2) meets the
definition of a commercial solid waste;
and (3) is not eligible for any
exemptions under NSPS subpart CCCC.
In addition, NSPS subpart CCCC applies
as a result of the date construction
began on the incinerator.
Abstract for [M100012]
Q: If Riceland Cabinet’s (Riceland)
facility in Orville, Ohio, which is
subject to 40 CFR part 63, subpart JJ,
relocates its facility and reduces its
emission to area source status
thresholds after the NESHAP
compliance date, does it remain subject
to the MACT subpart JJ and Title V
Permitting requirements?
A: Yes. The relocated facility would
be considered an existing source under
MACT subpart JJ. The relocated facility
would also be required to obtain a Title
V Permit. The ‘‘Once In Always In’’
Policy (OIAI Policy) allows new sources
the option to comply with federally
enforceable limits after the compliance
date in order to not be subject to the
NESHAP. However, a relocated facility
cannot be defined as a new source for
the purposes of the NESHAP. To be
considered a new source, a source
would have to be constructed after the
compliance date; however, relocating a
facility is not construction according to
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NESHAP definition of construction.
Construction is defined as the on-site
fabrication, erection, or installation of
an affected source. Construction does
not include the removal of all
equipment comprising an affected
source from an existing location and
reinstallation of such equipment at a
new location. Any source that is not a
new source is defined as an existing
source.
Abstract for [1000012]
Q: Does EPA approve the use of
alternative method ASTM D975–07b for
fuel certification under 40 CFR part 60,
subpart Dc, in lieu of ASTM D396 for
Quest Diagnostics in Chantilly,
Virginia?
A: Yes. ASTM D975–07b is more
stringent than ASTM D396 in all cases
except viscosity, which will not affect
sulfur dioxide emissions, and thus is
acceptable under NSPS subpart Dc.
Abstract for [1000013]
Q1: Is Method 7E an allowable
alternative test method for measuring
nitrogen oxide (NOx) emissions at nitric
acid plants for the purposes of
determining compliance with 40 CFR
part 60, subpart G?
A1: No. Method 7E is not approved
for use to demonstrate compliance with
NSPS subpart G.
Q2: Is Method 6C an allowable
alternative test method for measuring
sulfur dioxide (SO2) emissions at
sulfuric acid plants for the purposes of
determining compliance with 40 CFR
part 60, subpart H?
A2: No. Method 6C is not approved
for use to demonstrate compliance with
NSPS subpart H.
Abstract for [1000015]
Q: Will EPA reconsider its February 8,
2006 determination that 40 CFR part 60,
subpart KKKK, applies to a turbine at
Great River Energy in Cambridge,
Minnesota?
A: No. The request does not provide
any new information that would cause
the Agency to reconsider the February 8,
2006 determination that NSPS subpart
KKKK applies.
Abstract for [1000016]
Q: Did construction commence on the
proposed installation of a gas turbine at
Great River Energy (GRE) in Cambridge,
Minnesota, before the applicability date
of 40 CFR part 60, subpart KKKK?
A: No. GRE did not begin installation
of the turbine nor enter into a
contractual obligation to undertake and
complete within a reasonable time a
continuous program of construction for
the installation of the turbine prior to
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the applicability date of 40 CFR part 60,
subpart KKKK.
Abstract for [1000017]
Q1: Is the installation of a capacitor
bank and tuned reactor at the electrical
substation servicing an electric arc
furnace (EAF) at the Alton Steel, Inc.
facility, a physical or operational change
to an existing EAF under 40 CFR 60.14
of the General Provisions?
A1: Yes. The capacitor/reactor project
increased the capacity (i.e., the
production rate) of the existing EAF and
is therefore an operational change to the
EAF under 40 CFR 60.14, which
resulted in a kilogram per hour increase
in the emission rate of particulate
matter.
Q2: Is the capacitor/reactor project
exempt from the definition of
‘‘modification’’ because it is ‘‘routine
maintenance, repair, or replacement’’
under 40 CFR 60.14(e)(1)?
A2: No. The capacitor/reactor project
was not routine maintenance, repair, or
replacement under 40 CFR 60.14(e)(1).
Q3: Is the capacitor/reactor project not
subject to 40 CFR part 60, subpart AAa
because it is not considered
‘‘modification’’ based on the capital
expenditure exemption at 40 CFR
60.14(e)(2)?
A3: Yes. The capacitor/reactor project
allowed the EAF to increase the rate of
production but involved no capital
expenditure on the ‘‘existing facility’’
(i.e., the EAF as it is defined at 40 CFR
60.271(a)). All of the monetary
expenditure associated with the project
involved replacing components and
adding new components to the electrical
substation that supplies power to the
EAF. Because the capital expenditure
exemption at 40 CFR 60.14(e)(2) applies,
the capacitor/reactor project has not
triggered the applicability of NSPS
subpart AAa.
wwoods2 on DSK1DXX6B1PROD with NOTICES_PART 1
Abstract for [1000019]
Q1: Does 40 CFR part 60, subpart
AAAA, apply to the syngas gasification
process at Fulcrum BioEnergy’s
(Fulcrum) proposed facility in
McCarran, Nevada?
A1: No. Because Fulcrum’s proposed
syngas gasification process is neither
combustion nor pyrolysis, the syngas
generation unit is not considered a
‘‘pyrolysis/combustion unit’’ or
‘‘municipal waste combustion unit’’ as
defined in NSPS subpart AAAA.
Q2: Does 40 CFR part 60, subpart
AAAA, apply to the combined cycle
combustion turbine if the facility meets
the requirements for the small power
production facility exemption or the
cogeneration facility exemption?
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A2: No. 40 CFR 60.1020(b) and (c) list
the requirements that a facility must
meet to be exempt from NSPS subpart
AAAA as a small power production
facility or cogeneration facility. Those
requirements include meeting criteria
established by the Federal Power Act,
combusting homogeneous waste, and
providing notification and
documentation to EPA. EPA concurs
with Fulcrum’s assessment that the
gasified waste would be considered
homogeneous. However, to qualify for
either of the facility exemptions
Fulcrum would also need to provide
appropriate notification and
documentation that it meets the criteria
established by the Federal Power Act.
Q3: Does 40 CFR part 60, subpart
AAAA, apply to the air pollution
control flare?
A3: No. As long as the flare is
operated solely as an air pollution
control device, it is excluded from the
definition of ‘‘municipal waste
combustion unit’’ under NSPS subpart
AAAA.
Abstract for [M100014]
Q: Does EPA approve NuStar Logistics
(‘‘NuStar’’) request for alternative
monitoring of emissions under 40 CFR
part 63, subpart R, of continuous
presence of a pilot flame for the vapor
combustion unit (VCU) in lieu of
temperature monitoring at the firebox at
its bulk gasoline terminal in Colorado
Springs, Colorado?
A: EPA does not approved NuStar
alternative monitoring request because
it does not demonstrate meeting the
requirements of 40 CFR 63.8(f)(4),
63.427(a)(5), and 63.428(c)(3)).
Additional information needs to be
provided within 30 calendars days after
receipt of this letter. [Additional
information was not provided.]
Abstract for [M100015]
Q: Does EPA approve the request of
the Tooele Chemical Agent Disposal
Facility (TOCDF) in Stockton, Utah, to
waive the requirement to establish, and
subsequently monitor, at the
Deactivation Furnace System (DFS), a
12-hour rolling average (HRA) feed rate
for mercury, ash, semi- and low-volatile
metals, and chlorine required by 40 CFR
63.1290(l), (m), (n), and (o),
respectively?
A: EPA conditionally approves
TOCDF’s request to waive the
requirement to establish, and
subsequently monitor, at the DFS, a 12–
HRA feed rate for mercury, ash, semiand low-volatile metals, and chlorine
required by 40 CFR 63.1290(l), (m), (n),
and (o), respectively. EPA’s approval is
limited to when burster and fuze pairs
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from 4.2″ HD mortars, HT mortars, and
minimal amounts of process generated
waste such as agent contaminated rags
and small metal parts are fed to the DFS.
Additionally, EPA’s approval is based
on a feed rate to the DFS of combined
4.2″ mortar burster/fuze pairs of 274/
hour, as well as the RCRA Permit limits
for process generated waste, and
TOCDF’s commitment to monitor and
comply with those limits.
Abstract for [M100016]
Q: Does EPA approve the request of
the Tooele Chemical Agent Disposal
Facility (TOCDF) located in Stockton,
Utah, under 40 CFR part 63, subpart
EEE, to modify the first condition of the
approved alternative monitoring request
(AMR) of April 27, 2006, to also include
munitions processing? The first
condition states that ‘‘this approval
shall apply only to the Baseline
Processing phase of the TOCDF Mustard
campaign which restricts processing to
only those ton containers (TCs) in
which the level of Hg in the liquid
phase is less than 1 ppm’’?
A: Yes. EPA approves modifying the
scope of the AMP request to include the
processing of the above TCs, munitions,
and secondary waste. Based on the
information provided, EPA believes that
TOCDF can process the additional TCs,
munitions, and secondary waste and
maintain compliance with 40 CFR part
63, subpart EEE standards.
Abstract for [M100017]
Q: Does EPA approve under 40 CFR
part 63, subpart EEE, the request of the
Tooele Chemical Agent Disposal
Facility (TOCDF) in Stockton, Utah, to
modify Condition #2 of the alternative
monitoring request approved by EPA on
June 29, 2009? The condition states
among other things, that during the
Non-Baseline Processing Phase, the
sampling period for the Appendix K
System sorbent tube trap sets shall be no
greater than 12 hours, and Tooele
requests to change ‘‘no greater than 12
hours’’ to ‘‘no greater than 12 hours
(plus or minus 30 minutes to allow for
unforeseen events)’’?
A: EPA approves the revision to
Condition #2 because TOCDF has
confirmed that even though the start or
stop time may vary by up to 30 minutes,
TOCDF will sample continuously. For
those periods where the start or stop
time varies by 15 minutes or more,
TOCDF will provide a reason code in its
reporting to explain why sampling was
plus or minus 15 minutes or more. In
addition, EPA believes the change in
Condition #2 is approvable for the
reasons expressed in its June 29, 2009
letter.
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Abstract for [M100018]
Q1: Does EPA approve Albemarle
Corporation’s (Albemarle) alternative
monitoring request for its facility in
Orangeburg, South Carolina, to measure
the liquid temperature in the receiver of
its process condensers as described in
40 CFR 63.2460(c)(2)(v) when
conducting the process condenser
demonstration required by 40 CFR
63.1257(d)(3)(iii)(B)?
A1: Yes. EPA agrees that measuring
the liquid temperature of the condensed
liquid in the receiver would be an
acceptable alternative to measuring the
exhaust gas temperature as required by
40 CFR 63.1257(d)(3)(iii)(B) because the
temperature of the condensed liquid
and the exhaust gas are in equilibrium.
Q2: Does EPA approve Albemarle’s
alternative recordkeeping request under
40 CFR part 63, subpart GGG, to
maintain records of standard and nonstandard batch production to allow the
calculation of rolling annual emissions
on a daily basis to comply with the
daily rolling 365-day HAP emissions
once per month as required by 40 CFR
63.1259(b)(4)?
A2: Yes. For purposes of compliance
with the annual mass limits of 40 CFR
63.1254(a)(2) and (b)(2), Albemarle must
calculate and record the daily rolling
annual total emissions for the previous
month by the fifth day of each month.
Q3: Does EPA approve Albemarle’s
request for a waiver of the performance
test requirements of 40 CFR
63.11(b)(6)(i) for a flare used to control
Hydrogen Cyanide (HCN) emissions
from the HCN Pharmaceutical
Manufacturing Process Unit (PMPU)?
A3: Yes. EPA approves a waiver of the
requirement to conduct a performance
test to demonstrate compliance with 40
CFR 63.11(b)(6)(i). This waiver is for the
same flare being operated under the
same conditions for which Albemarle
submitted information in 2002 and 2003
to support its request for a waiver of the
performance test requirements under 40
CFR 60.18(c)(3)(i). In addition, the
regulatory language of 40 CFR.11(b)(6)(i)
is identical to that of 40 CFR
60.18(c)(3)(i).
Q4: Does EPA approve Albemarle’s
setting alternate operating limits for a
hydrochloric acid (HCl) bubbler control
device to those required by 40 CFR
63.1258(b)(1)(ii) for scrubbers?
A4: EPA conditionally approves the
alternate operating parameters pending
a successful performance test and other
conditions listed in the EPA response
letter.
Abstract for [1000021]
Q: Do the requirements for external
floating roof tanks (EFR) in 40 CFR
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Abstract for [1000022]
Q1: Is a municipal solid waste landfill
that already has a design capacity equal
to or greater than 2.5 million megagrams
and 2.5 million cubic meters required
under 40 CFR part 60, subpart WWW,
to submit an amended design capacity
report upon approval of a further
expansion?
A1: No. The facility is not required to
do so as it is subject to the standards 40
CFR 60.752(b), which does not require
such reports.
Q2: Is a municipal solid waste landfill
that already has a design capacity equal
to or greater than 2.5 million megagrams
and 2.5 million cubic meters required
under 40 CFR part 60, subpart WWW,
to submit a notice for a physical or
operation change pursuant to 40 CFR
60.7(a)(4) upon approval of a further
expansion?
A2: Yes. Under NSPS subpart WWW,
the facility is required to do so for all
modifications that meet the definition of
40 CFR 60.14.
asbestos containing material is not
subject to any process or treatment that
would convert it to a nonasbestos
material, there is no conversion to a non
asbestos material taking place.
Q2: Are the notification requirements
at 40 CFR 61.145 applicable to the
removal of asbestos covered and coated
stator bars at the site where they are
removed and at the site where the
asbestos is stripped from the bars?
A2: At each site where the stator bars
are removed, if the surface area (of the
bars to be removed) covered with
asbestos containing resin and tar equals
or exceeds 160 square feet, then the
notification requirements of 40 CFR
61.145 apply and a notice must be
submitted to the Federal, State or local
agency delegated to receive such
notifications. Because the stator bars
will be stripped of asbestos at a site in
Ashtabula, Ohio, a copy of each
notification for bars removed outside of
Ohio should also be sent to the Ohio
Environmental Protection Agency. No
matter where the bars are removed, a
notification must be in place for each
batch of stator bars stripped of asbestos
containing materials at the site in
Ashtabula, Ohio.
Q3: Which sections of 40 CFR
61.145(c) apply at the site where the
stator bars are removed?
A3: Because the stator bars are not
going to be stripped of asbestos at the
site where they are removed, and
because the stator bars are going to be
shipped to Ashtabula, Ohio, the bars
must be handled in accordance with the
requirements of 40 CFR 61.145(c)(5)(i)
through (iii).
Abstract for [A100001]
Q1: Does the removal of asbestos
containing coating materials from stator
bars at a metal recycling facility in
Ashtabula, Ohio, constitute an asbestos
conversion process subject to 40 CFR
61.155?
A1: No. 40 CFR 61.155 applies to
situations where regulated asbestos
containing material, and asbestoscontaining waste material, is converted
to a non-asbestos material. The
information provided by the requestor
indicates that stator bars coated with an
asbestos containing resin and wrapped
with tape covered by an asbestos
containing tar will be removed from
various locations and the bars will be
taken to a recycling operation where the
asbestos containing resin and tar will be
removed from the bars. All of the
asbestos that is removed from the stator
bars will remain asbestos after it is
removed from the bars. The asbestos
material that is removed will be
disposed of in a landfill. Because the
Abstract for [M100019]
Q: With respect to the operating limits
for cold core machines utilizing capture
and wet acid scrubbers to control
triethylamine (TEA) emissions at the
Indianapolis Casting facility in
Indianapolis, Indiana: When dampers
are manually set in a fixed position,
does the exemption from the continuous
parameter monitoring system (‘‘CPMS’’)
requirement apply only to exempting a
CPMS with regard to damper position or
would a fixed damper position exempt
the cold core machine capture system
from monitoring the hourly average rate
as with respect to 40 CFR 63.7740(a)?
A: 40 CFR 63.7710(b)(2)(i) contains
two different requirements (at a
minimum) for the capture system: level
of ventilation draft and damper position
settings. Both types of CPMS are
required, but the CPMS for damper
system is not needed if the damper
position is manually set and in a fixed
position. Thus, the CPMS exemption
referred to in 40 CFR 63.7740(a)(2)
60.112b(a)(2), the requirements for
internal floating roof (IFR) tanks in 40
CFR 112b(a)(1) apply, or both, apply to
EFR tanks which have been enclosed
with a fixed roof located at the
TransMontaigne Operating Company LP
facility in Selma, North Carolina?
A: An EFR tank which is enclosed by
the installation of a fixed roof meets the
40 CFR part 60, subpart Kb description
of an IFR tank and is therefore subject
to the requirements for IFR tanks. An
enclosed EFR tank is no longer subject
to the NSPS subpart Kb requirements for
EFR tanks.
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applies solely to the installation of a
CPMS for damper position.
Abstract for [1000023]
Q: Does EPA approve a request for
alternate performance testing under 40
CFR part 60, subpart KKKK, for
combustion turbines and direct-fired
heaters being installed as part of a
process modification at the PL
Propylene facility in Houston, Texas?
A: Yes. EPA has determined that the
stationary combustion turbines are
subject to the requirements of NSPS
subpart KKKK, and has approved the
request to conduct one performance test
downstream of the selective catalytic
reduction units, and to apply reference
method results from the NOx
continuous monitoring system
certification for the initial
demonstration of compliance with 40
CFR 60.4320. However, testing must be
conducted using the fuel or combination
of fuels that would result in the highest
emissions.
Abstract for [1000024]
Q. Is the proposed Earth Energy oil
sand mine and processing facility in
eastern Utah, which will include mining
of the naturally occurring oil sands and
extraction of the bitumen from these
sands, subject to 40 CFR part 60, subpart
Ja?
A: No. The Earth Energy facility
would not be considered a ‘‘petroleum
refinery’’ and thus is not subject to
NSPS subpart Ja.
wwoods2 on DSK1DXX6B1PROD with NOTICES_PART 1
Abstract for [M100020]
Q1: Does EPA approve the Tooele
Army Depot’s (TEAD’s) request to
establish a limit on the minimum
baghouse inlet temperature to replace
the requirement to establish a limit on
the maximum baghouse temperature (40
CFR 63.1209(k)(1)(i)) to assure
compliance with the dioxin and furan
limit in 40 CFR 63.1219(a)(1)?
A1: EPA conditionally approves the
use of a minimum baghouse inlet
temperature rather than a maximum
baghouse inlet temperature during the
Comprehensive Performance Test if the
baghouse inlet temperature is maintain
at the required level, as established in
the EPA response letter.
Q2: Does EPA approve TEAD’s
request to establish a limit on the
maximum afterburner outlet
temperature to replace the requirement
to establish a limit on the maximum
baghouse inlet temperature (40 CFR
63.1209(n)(1)) to ensure compliance
with the semi-volatile and low volatility
metals limits in 40 CFR 63.1219(a)(3)
and (4)?
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A2: No. EPA cannot approve the
request because the temperature range
of the inlet to the baghouse can vary so
dramatically.
Q3: Does EPA approve TEAD’s
request to establish the maximum
potential particulate matter (PM)
generation as a limit to replace the
requirement to establish the maximum
ash feed rate limit to ensure compliance
with 40 CFR 63.1219(a)(7)?
A3: Yes. EPA conditionally approves
the request to establish the maximum
potential particulate matter (PM)
generation as a limit to replace the
requirement to establish the maximum
ash feed rate limit, provided that (i) The
propellants, explosives and
pyrotechnics (PEP) feed rate will not
exceed 56.28 lb/hr and (ii) the PM
generation will not exceed the worst
case theoretical maximum based on the
PEP feed rate above.
Abstract for [M100021]
Q1: Does EPA approve of the operator
of a secondary aluminum continuous
caster at the Commonwealth Aluminum
Concast (Commonwealth) facility in
Uhrichsville, Ohio, weighing the metal
by measuring the volume of the slab
produced by the continuous caster even
if the method does not meet the one
percent accuracy requirement at 40 CFR
63.1510(e)?
A1: Yes. Although these accuracies do
not meet the one percent accuracy
requirement at 40 CFR 63.1510(e), EPA
has concluded that on the basis of the
information provided the affected
source should be able to meet the
relevant emission standard.
Q2: May the operator record and
report on a 24-hour basis the chlorine
injection rate for its in-line fluxers since
the chlorine meter is not accurate to one
percent for the 15-minute block time
period intervals specified in the rule at
40 CFR 63.1510(j)?
A2: No. In this instance, available
data indicate that the required one
percent accuracy can be achieved on a
16-hour basis. Therefore, EPA
determines that there is no basis for
extending the averaging period beyond
16 hours.
Q3: May the operator test only one of
two identical in-line fluxers to measure
particulate matter emissions?
A3: Yes. Because the in-line casters
operate in series, the test plan does not
contemplate testing of PM emissions
from each fluxer individually. For the
purposes of compliance calculations,
however, the particulate matter is
assumed to emit from the tested caster.
This would represent a conservative
worst-case assumption, and does not
require the assumption that an equal
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amount of particulate matter is emitted
from each caster.
Q4: May the operator conduct
performance testing for two of the four
aluminum melting furnaces?
A4: Yes. EPA approves the testing of
two of a total of four of the aluminum
melting furnaces if these have the same
physical dimensions and capacity, and
the operator charges each furnace with
the same materials and the same
reactive fluxing agents in the same
proportions, and this will maintain
identical work practices. Also,
Commonwealth will perform three test
runs for two representative furnaces
during a complete operating cycle,
which is defined for purposes of this
testing as the initial metal charging
through the final skim, or about 1.5
hours. In addition, each melting furnace
(M1 through M4) has the same physical
dimensions and capacity of 233,000
tons, and maximum 21 million Btu/hour
heat input natural gas burners. The
testing of emissions from M1 will be
representative of emissions from M3,
and the testing of emissions from M2
will be representative of emissions from
M4.
Abstract for [M100022]
Q1: Does EPA approve the revised
comprehensive performance test plan
(CPT) and continuous monitoring
system (CMS) performance evaluation
test (PET) plan for Sunoco Chemicals, in
Haverhill, Ohio, pursuant to 40 CFR
63.1207(e)(1)(i)(A)?
A1: Yes. EPA approves Sunoco’s
revised CPT and CMS PET plan under
MACT subpart EEE.
Q2: Does the requirement for a onetime dioxin/furan test apply to Boiler
UC pursuant to 40 CFR 63.1207(b)(3)(ii)
and 63.1207(b)(3)(iii)?
A2: EPA concludes that the
requirement for a one-time dioxin/furan
test for Boiler UC does not apply until
Sunoco resumes generation and
incineration of its two hazardous waste
feedstreams.
Q3: Does EPA approve Sunoco’s PM
DIL requests for Boiler UC?
A3: Yes. EPA approves Sunoco’s PN
DIL requests for Boiler UC.
Q4: Does EPA approve Sunoco’s
request to use data from a 2006 DRE test
on Boiler UC as documentation of
conformance with the applicable DRE
emission standard for Boiler UC
pursuant to 40 CFR 63.1207(c)(2)?
A4: Yes. EPA approves Sunoco’s
request to use data from a 2006 DRE test
on Boiler UC as documentation of
conformance with the applicable DRE
emission standard for Boiler UC.
Q5: Does EPA approve Sunoco’s
request to use data from a November
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2001 DRE test on Boiler UE as
documentation of conformance with the
applicable DRE emission standard for
Boiler UE pursuant to 40 CFR
63.1207(c)(2)?
A5: Yes. EPA approves Sunoco’s
request to use data from a November
2001 DRE test on Boiler UE as
documentation of conformance with the
applicable DRE emission standard for
Boiler UE pursuant to 40 CFR
63.1207(c)(2).
Q6: Does EPA approve a maximum
theoretical emission concentration
request for Boiler UC and Boiler UE
pursuant to 40 CFR 63.7(h) and
63.1207(m)?
A6: Yes. EPA approves a maximum
theoretical emission concentration
request for Boiler UC and Boiler UE
pursuant to 40 CFR 63.7(h) and
63.1207(m).
wwoods2 on DSK1DXX6B1PROD with NOTICES_PART 1
Abstract for [1000025]
Q1: Are the flow monitoring
procedures under 40 CFR part 60,
subpart RRR, an acceptable alternative
to the 40 CFR part 60, subpart NNN,
requirements for the distillation
operation at Flint Hills’ facility in Saint
Paul, Minnesota?
A1: Yes. EPA finds that in this
instance the NSPS subpart RRR flow
monitoring procedures are an acceptable
alternative to those under NSPS subpart
NNN. The NSPS subpart RRR
requirement to monitor diversions from
the control device accomplishes the
same result (i.e., providing a record of
when vent streams are not controlled) as
the NSPS subpart NNN requirement to
monitor the flow to the control device.
Q2: Does EPA approve the use of
certain monitoring, recordkeeping, and
reporting provisions under 40 CFR part
60, subpart RRR, as alternative
monitoring requirements to those under
40 CFR part 60, subpart NNN, for the
Flint Hills’ facility in Saint Paul,
Minnesota?
A2: Yes. EPA approves the use of the
provisions in NSPS subpart RRR as an
alternative means of demonstrating
compliance under NSPS subpart NNN
for the specified distillation unit. As
conditions of approval, the facility must
comply with the recordkeeping and
reporting requirements for flow
indicators in NSPS subpart RRR and
must maintain a schematic diagram for
all related affected vent streams,
collection system(s), fuel systems,
control devices, and bypass systems as
stated in 40 CFR 60.705(s).
Q3: Does EPA approve a waiver of
initial performance tests for certain
boilers and heaters at the Flint Hills’
facility in Saint Paul, Minnesota?
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A3: Yes. Pursuant to 40 CFR
60.8(b)(4), EPA conditionally approves
the performance test waiver for the
boilers and process heaters which are
fired with fuel gas containing a vent
stream from the Poly Unit DePropanizer (43V–5), Saturates Gas DePropanizer (43V–19), and Alky Unit DePropanizer (35V–2). This waiver is
applicable for boilers and process
heaters that meet the definitions of a
boiler or process heater in 40 CFR
60.701. Both the alternative monitoring
and the waiver of performance testing
are contingent upon the vent streams
being vented to a fuel gas system and
introduced into the flame zone with the
primary fuel.
Q4: Does EPA approve Flint Hills’
request for alternate flare reporting
required by 40 CFR 60.665(l)(4), Subpart
NNN?
A4: Yes. EPA approves Flint Hills
Resources’ (FHR’s) request to comply
with the reporting requirements on the
status of the pilot flame in 40 CFR
63.654(g)(6)(i)(B) of Subpart RRR in lieu
of the flare requirements in 40 CFR
60.665(l)(4) of Subpart NNN, based on
approval of the AMP request.
Abstract for [M100023]
Q: What is considered a comparable
new source under 40 CFR Part 63,
Subpart PPPPP, when determining if
reconstruction has occurred under 40
CFR 3.2 of the General Provisions at
John Deere’s engine testing facility in
Dubuque, Iowa?
A: While the regulations do not define
‘‘comparable new source,’’ it is clear
within context of the paragraph (see
63.2, reconstruction definition) that the
term stands for ‘‘a newly reconstructed
existing facility.’’ EPA has determined
that the addition of the new test cells
equipment to a facility, as defined in 40
CFR part 63, Subpart PPPPP, does not
automatically trigger new source MACT
requirements, unless the definition of
reconstruction as listed in 40 CFR 63.2
is met. Based on the information
provided, EPA has determined that for
the John Deere Facility the cost of new
equipment is not more than 50 percent
of the cost to construct a comparable
new facility. Therefore, the definition of
reconstruction would not be met and
new source MACT requirements were
not triggered. The percent cost of
installation should be calculated by
dividing the cost of new components
(i.e., new test cell equipment) by the
cost of a newly reconstructed existing
facility (i.e., cost of existing test cells
and existing equipment) to determine if
the cost criterion in the definition of
reconstruction at 40 CFR 63.2 is met.
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Abstract for [M100024]
Q1: How does the vacatur of the
startup, shutdown, and malfunction
(SSM) exemption provisions of 40 CFR
part 63, subpart A, impact the reporting
requirements of 40 CFR part 63, subpart
RRR?
A1: In general, the SSM vacatur
should have no impact on the reporting
requirements in MACT subpart RRR.
Q2: If a monitoring malfunction
occurs that does not cause excess
emissions, is it a reportable occurrence?
A2: Yes, all malfunctions are required
to be reported regardless of the resulting
emissions.
Abstract for [1000026]
Q: Does EPA approve the request of
the Enbridge Energy facility in Superior,
Wisconsin, to perform an internal
inspection under 40 CFR part 60,
subpart Kb, on the internal floating roofs
(IFR) tanks while they are in-service and
out-of-service?
A: Yes. Enbridge Energy may perform
an internal inspection by visually
inspecting the IFR components from the
top of the IFR using inspection
procedures that are similar to those
found in 40 CFR 63.1063(d)(1) and 40
CFR part 63, subpart WW. The proposed
alternative monitoring procedure, based
on 40 CFR part 63, subpart WW, would
serve to satisfy the requirements of 40
CFR 60.113b(a)(4).
Abstract for [Z100001]
Q: Are sour water streams managed in
sour water strippers regulated upstream
of the sour water stripper exit under 40
CFR part 61, subpart FF?
A: Yes. Assuming that the total
annual benzene quantity from facility
waste is 10 Mg/year or greater, as
provided by 40 CFR 61.342(b), the
facility must comply with the
requirements of 40 CFR 61.342 (c)–(h).
Thus, these requirements would apply
to sour water streams managed
upstream of the sour water stripper exit.
Abstract for [M100025]
Q: Does EPA approve the request of
Ross Incineration Services in Grafton,
Ohio, for the hazardous waste
incinerator operator to use alternate
operating parameters in lieu of flow rate
measurements for the scrubbers to avoid
automatic waste feed cutoffs should a
flow meter fail pursuant to 40 CFR part
63 subpart EEE?
A: Yes. EPA conditionally approves
this request based upon the review of
the data submitted showing that the
alternate operating parameters,
specifically, scrubber temperatures,
water pump current, and nozzle
pressure, can be measured and
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Federal Register / Vol. 76, No. 119 / Tuesday, June 21, 2011 / Notices
maintained within a normal operating
range, thereby assuring the performance
of scrubber water pumps. The approval
is contingent upon the ability of the
facility to continuously maintain the
scrubber flow rates for the radial-flow
scrubber (RFS) and the gas-liquid
contactor (GLC).
Metal Parts Furnace (MPF), and to add
the Manual Hg Emission Measurement
method on the Liquid Incinerators
(LICs)?
A: Yes. EPA conditionally approves
the request, provided that the facility
meets all of the conditions set out in the
EPA response letter.
Abstract for [M100026]
Q: Does EPA approve the request of
the Tooele Chemical Agent Disposal
Facility (TOCDF) in Stockton, Utah, to
modify conditions of the alternative
monitoring request (AMR) approved by
EPA on June 29, 2009, pursuant to 40
CFR part 63, subpart EEE, with regards
to the use of a thermal desorption
mercury analyzer and mercury sampling
timeframes?
A: Yes, EPA approves revisions to
applicable conditions of the June 26,
2009 AMR approval. All conditions of
approval are restated in the current
AMR approval.
Abstract for [A110001]
Q1: If a city, county, municipality
undertakes an ‘‘urban renewal’’ project
that demolishes or renovates multiple
single family homes, is it subject to the
asbestos NESHAP regulation, NESHAP
subpart M?
A1: It may be subject to the asbestos
NESHAP. The city, county or
municipality may be the owner or
operator, depending upon the situation.
As the owner or operator, the
government entity must conduct a
thorough inspection of each home that
is identified to be demolished or
renovated for the project. If the
combined amount of friable asbestos or
asbestos that will be made friable during
the demolition or renovation operation
exceeds the regulated threshold, then
the demolition or renovation operation
must comply with the air emission, the
waste management, and the disposal
requirement of the asbestos NESHAP.
Q2: Are single family homes not
subject to the asbestos NESHAP based
on the 1995 Clarification of Intent
which described how isolated single
family homes were exempt from the
asbestos NESHAP?
A2: As stated in the question, the
Clarification of Intent describes how to
determine an isolated single family
home. The ‘‘urban renewal’’ projects are
not about isolated homes but a group of
homes as part of a project that will be
demolished or renovated over a period
of time. In the preamble to the 1990
asbestos NESHAP amendments, EPA
did not consider residential structures
that are demolished as part of a
commercial or public project to be
exempt from this rule.
Q3: What is or please define
‘‘planning period?’’
A3: Planning period is not defined in
the asbestos NESHAP regulation.
Planning period was identified in the
1995 Clarification of Intent to provide
guidance when considering single
family homes being demolished, and
whether the home was considered a
facility under the demolition operation.
Demolition or renovation operations
planned at the same time or as part of
the same planning period or scheduling
period are considered to be part of the
same project, and that in the case of
municipalities, a planning or scheduling
period is often a fiscal or calendar year
wwoods2 on DSK1DXX6B1PROD with NOTICES_PART 1
Abstract for [M100027]
Q: Does EPA approve the request of
the Tooele Chemical Agent Disposal
Facility (TOCDF) in Stockton, Utah, to
comply with the mercury emission
standard (130 micrograms/dscm,
corrected to 7 percent oxygen) at the
Metal Parts Furnace (MPF) by: 1)
continuously collecting exhaust gas
samples and sampling for mercury (Hg)
and taking the rolling average of the
results obtained from three consecutive
4-hour sampling events, resulting in a
12-hour averaging period for
compliance determination purposes,
rather than relying on an operating
parameter limit (OPL) for a maximum
Hg feedrate as required by 40 CFR
63.1209(l)(1)(i); and (2) continuously
sampling exhaust gas samples using a
modified EPA method approved for use
by coal-fired power plants found at 40
CFR Part 75, Appendix K rather than
using Method 29 for Hg emissions, as
required by 40 CFR 63.1208(b)(2)?
A: Yes. EPA conditionally approves
the request provided that the facility
meets all of the conditions set out in the
EPA response letter.
Abstract for [M100028]
Q: Does EPA approve the request of
the Tooele Chemical Agent Disposal
Facility (TOCDF) in Stockton, Utah, to
modify some of the Conditions of
Approval contained in determination
letters issued by EPA on April 27, 2006
and September 24, 2007 approving
previously submitted alternative
monitoring requests (AMRs) pertaining
to the Manual Mercury (Hg) Emission
Measurement method used during the
Mustard Agent Processing in TOCDF’s
VerDate Mar<15>2010
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36129
or the term of a contract. The fact that
demolitions might be spread out over
multiple fiscal or calendar years or even
multiple contracts, however, does not
necessarily mean they are not occurring
as part of the same planning period.
Dated: March 10, 2011.
David Hindin,
Acting Director, Office of Compliance.
[FR Doc. 2011–15416 Filed 6–20–11; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
[FRL–9321–3]
Underground Injection Control
Program; Hazardous Waste Injection
Restrictions; Petition for Exemption—
Class I Hazardous Waste Injection;
ExxonMobil Environmental Services
Company, Pasadena TX
Environmental Protection
Agency (EPA).
ACTION: Notice of a final decision on a
no migration petition.
AGENCY:
Notice is hereby given that an
exemption to the land disposal
Restrictions, under the 1984 Hazardous
and Solid Waste Amendments to the
Resource Conservation and Recovery
Act, has been granted to ExxonMobil
Environmental Services Company for
two Class I injection wells located at
Pasadena, Texas. The company has
adequately demonstrated to the
satisfaction of the Environmental
Protection Agency by the petition and
supporting documentation that, to a
reasonable degree of certainty, there will
be no migration of hazardous
constituents from the injection zone for
as long as the waste remains hazardous.
This final decision allows the
underground injection by ExxonMobil,
of the specific restricted hazardous
wastes identified in this exemption, into
Class I hazardous waste injection wells
No. WDW–397 and WDW–398 at the
Agrifos Pasadena Texas Fertilizer
facility, Pasadena, Texas, until
December 31, 2020, unless EPA moves
to terminate this exemption. Additional
conditions included in this final
decision may be reviewed by contacting
the Region 6 Ground Water/UIC Section.
A public notice was issued April 19,
2011. The public comment period
closed on June 6, 2011. No comments
were received. This decision constitutes
final Agency action and there is no
Administrative appeal. This decision
may be reviewed/appealed in
compliance with the Administrative
Procedure Act.
SUMMARY:
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Agencies
[Federal Register Volume 76, Number 119 (Tuesday, June 21, 2011)]
[Notices]
[Pages 36121-36129]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2011-15416]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
[FRL-9321-1]
Recent Posting to the Applicability Determination Index (ADI)
Database System of Agency Applicability Determinations, Alternative
Monitoring Decisions, and Regulatory Interpretations Pertaining to
Standards Under the Clean Air Act
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
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 Office of Enforcement
and Compliance Assurance (OECA) Web site at: https://www.epa.gov/compliance/monitoring/programs/caa/adi.html. The document 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 e-mail at: malave.maria@epa.gov. For
technical questions about the 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 to the NSPS in 40 Code of Federal
Regulations (CFR) Part 60 and the General Provisions to 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 [which includes Maximum Achievable Control Technology
(MACT) standards] and section 111(d) of the Clean Air Act (CAA)
regulations contain no specific regulatory provision that sources may
request applicability determinations, EPA responds to written inquiries
regarding applicability for the part 63 and section 111(d) programs as
well. The NSPS and NESHAP also allow sources to seek permission to use
monitoring or recordkeeping that are 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 on the ADI on a quarterly basis. 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. The letters and memoranda may be
searched by date, office of issuance, subpart, citation, control
number, or by string word searches.
Today's notice comprises a summary of 47 such documents added to
the ADI on May 25, 2011. The subject and header of each letter and
memorandum are listed in this notice, 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: https://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 May 25, 2011; the
applicable category; the subpart(s) of 40 CFR part 60, 61, or 63 (as
applicable) covered by 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 section 307(b)(1) of the
Clean Air Act. For example, this notice does not make an applicability
determination for a particular source into a nationwide rule. Neither
does it purport to make any document that was previously non-binding
into a binding document.
ADI Determinations Uploaded on April x, 2011
----------------------------------------------------------------------------------------------------------------
Control number Categories Subparts Title
----------------------------------------------------------------------------------------------------------------
M090044............................. MACT.................... A, RRR.................. Alternate Operating
Scenarios for
Production Furnace
1000001............................. NSPS.................... VVV..................... Installation of a
Pigment Mixing and
Milling Process
1000002............................. MACT, NSPS.............. AAAA, WWW............... Gas Treatment System
Used for Energy
Recovery Purposes
1000003............................. NSPS.................... WWW..................... Monitoring Lids of Gas
Well Sumps as
`Surface' of the
Landfill
M100001............................. MACT.................... EEEE.................... Once In Always In
Policy
M100002............................. MACT.................... MMMM.................... Use of Non-
Regenerative Carbon
Adsorption System
[[Page 36122]]
M100004............................. MACT.................... NNNNN................... Alternative Control
Device Operating
Parameters
M100005............................. MACT.................... FFFF, JJJ............... Solid State
Polymerization PET
Process
M100006............................. MACT.................... EEE..................... Excess Emissions
Reporting for a Waste
Liquid Fuel-Fired
Boiler
1000004............................. NSPS.................... A, Db................... Boiler Modification
1000007............................. NSPS.................... Y....................... Alternative Monitoring
1000008............................. NSPS.................... WWW..................... Landfill Gas Treatment
System
M100009............................. MACT.................... M....................... Secondary Carbon
Adsorption
Requirements for
Resold Equipment
1000009............................. NSPS.................... WWW..................... Landfill Gas Operating
Temperatures
M100010............................. MACT.................... EEE..................... Minimum Secondary
Combustion Chamber
Temperature Operating
Parameter Limit
1000011............................. NSPS.................... CCCC.................... Thermal Destruction
Unit Determination
M100012............................. MACT.................... JJ...................... Relocation of Facility
and Reduction of
Emissions after
NESHAP Compliance
Date
1000012............................. NSPS.................... Dc, IIII................ Alternative Method for
Fuel Supplier
Certification
1000013............................. NSPS.................... G, H.................... Use of Method 7E at
Nitric Acid Plants
and Method 6C at
Sulfuric Acid Plants
1000015............................. NSPS.................... KKKK.................... Commence Construction
for Gas Turbine
1000016............................. NSPS.................... GG, KKKK................ Commence Construction
for Gas Turbine
1000017............................. NSPS.................... A, AAa.................. Installation of a
Capacitor Bank and
Tuned Reactor
1000019............................. NSPS.................... AAAA.................... Conversion of Post-
Sorted Municipal
Solid Waste Feedstock
M100014............................. MACT.................... R....................... Alternative Monitoring
Plan
M100015............................. MACT.................... EEE..................... Alternative Monitoring
Plan
M100016............................. MACT.................... EEE..................... Modification of
Alternative
Monitoring Plan
M100017............................. MACT.................... EEE..................... Modification of
Alternative
Monitoring Plan
M100018............................. MACT.................... GGG..................... Alternative Monitoring
of Hydrochloric Acid
(HCl) Bubbler Control
Device
1000021............................. NSPS.................... Kb...................... External Floating Roof
Tank Enclosed with
Fixed Roof
1000022............................. NSPS.................... WWW..................... Amended Design
Capacity Reports
A100001............................. Asbestos................ M....................... Removal of Asbestos
Containing Coating
Materials from Stator
Bars
M100019............................. MACT.................... EEEEE................... Cold Core Machines
Used for Capture and
Wet Acid Scrubbers
1000023............................. NSPS.................... KKKK.................... Installation of
Combustion Turbines
and Direct-Fired
Heaters
1000024............................. NSPS.................... Ja...................... Mining of Naturally
Occurring Oil Sands
and Extraction of
Bitumen
M100020............................. MACT.................... EEE..................... Alternative Monitoring
Plan
M100021............................. MACT.................... RRR..................... Alternative Monitoring
Plan
M100022............................. MACT.................... EEE..................... Comprehensive
Performance Test Plan
1000025............................. NSPS.................... A, NNN, RRR............. Alternative Monitoring
Plan
M100023............................. MACT.................... PPPPP................... Appropriate Method for
Calculating
Reconstruction
M100024............................. MACT.................... RRR..................... Startup, Shutdown,
Malfunction Reporting
Requirements
1000026............................. NSPS.................... Kb...................... Alternative Monitoring
Plan
Z100001............................. NESHAP.................. FF...................... Sour Water Streams
Regulation
M100025............................. MACT.................... EEE..................... Alternative Operating
Parameters
M100026............................. MACT.................... EEE..................... Modification of
Alternative
Monitoring Plan
M100027............................. MACT.................... EEE..................... Alternative Monitoring
Plan
M100028............................. MACT.................... EEE..................... Modification of
Alternative
Monitoring Plan
A110001............................. NESHAP.................. M....................... Asbestos NESHAP:
Municipalities
demolishing and
renovating multiple
residential
structures as part of
an ``urban renewal''
project.
----------------------------------------------------------------------------------------------------------------
Abstracts
Abstract for [M090044]
Q1: Does 40 CFR part 63, subpart RRR, allow Kaiser Aluminum
Fabricated Products, Inc., the owner/operator of a secondary aluminum
production furnace, to switch back and forth between group 1 and group
2 furnace operation at a regular or even infrequent basis, depending on
what its being fed to the furnace at any given time, and turn the
control device on and off depending on the operating scenario?
A1: No. MACT subpart RRR does not allow for the furnace to be
designated group 1 and 2 at the same time, depending on what it's being
feed to the furnace. However, the owner/operator may choose to re-
designate a furnace on a very infrequent basis along with a permit
modification.
Q2: Does 40 CFR part 63, subpart RRR, allow an owner/operator to
operate the furnace as a group 1 furnace, accepting an undefined mix of
clean and purchased scrap and a fluxing agent, with the baghouse not
operating?
A2: No. A group 1 furnace cannot be authorized to operate under
more than one set of operating parameters depending on what is being
fed to the furnace at any given time and the use of a control device or
not. MACT subpart RRR addresses a single worst-case scenario when
conducting a performance test to establish operating parameters, and
does not address alternate operating scenarios.
Abstract for [1000001]
Q1: Are two mixing vessels and two milling machines being installed
at the Majilite facility in Dracut, Massachusetts, considered coating
mix preparation equipment under 40 CFR part 60, subpart VVV?
A1: Because Majilite's mixing vessels will be blending solvent with
other materials to prepare pigments that are used to prepare polymeric
coatings, the pigment mixing vessels are coating mix preparation
equipment subject to NSPS subpart VVV. The milling machines, however,
do not fit within the rule definition of coating mix preparation
equipment.
Q2: Majilite operates one coating line subject to NSPS, subpart
VVV, and that this coating line and coating mix
[[Page 36123]]
operation use more than 130 Mg of VOC per year. What are the
requirements under 40 CFR part 60, subpart VVV, for the coating mix
preparation equipment if the pigment mixing vessels are being installed
without concurrent construction of a control device?
A2: EPA has determined that because Majilite's subpart VVV coating
operation and associated coating mix preparation equipment use at least
130 Mg of VOC per 12-month period and the pigment mixing vessels are
being installed without concurrent construction of a control device,
Majilite must meet the requirements of 60.742(c)(2) for its pigment
mixing vessels, among other requirements.
Abstract for [1000002]
Q: Do the processes which occur in the preliminary treatment system
at Waste Management of New Hampshire's (WMNH) Turnkey Recycling and
Environmental Enterprise (TREE) facility in Rochester, New Hampshire,
meet the requirements for a ``treatment system'' under 40 CFR
60.752(b)(2)(iii)(C)?
A: Yes. EPA has determined that the preliminary treatment system
located at WMNH in which the gas has been compressed, dewatered, and
filtered down to 10 microns meets the criteria of a treatment system
under 40 CFR 60.752(b)(2)(iii)(C), and is not subject to the monitoring
and recordkeeping requirements of 40 CFR 60.756(b) and 40 CFR 60.758(b)
and (c).
Abstract for [1000003]
Q: Does EPA approve the request of Allied Imperial Landfill in
Imperial, Pennsylvania to monitor some landfill gas well sump structure
lids as though they were the ``surface'' of the landfill, in accordance
with 40 CFR part 60, subpart WWW?
A: Yes. EPA finds that monitoring the sump lids is adequate to
fulfill the requirements of NSPS subpart WWWW based on the intent of
NSPS subpart WWW and the sump structure construction. Monitoring inside
the sump structure could create an artificially elevated value for the
landfill gas well(s). If a landfill gas extraction well (LGFW)
monitoring event indicates readings above 500 ppm around the
circumference of the fiberglass structure, and/or lid of the structure,
then corrective actions must be completed, as required by NSPS subpart
WWW.
Abstract for [M100001]
Q: The Pactiv facility located in Winchester, Virginia, must comply
with 40 CFR part 63, subpart EEEE, the organic liquid distribution
(OLD) MACT, due to a hazardous air pollutant (HAP) in a foaming agent
used at the facility. Were the facility to switch the foaming agent to
one that uses less than 5 percent HAPS would the OLD MACT apply?
A: Yes. The new foaming agent still contains HAPs, and according to
the ``Once in Always In'' Policy, the OLD MACT still applies.
Abstract for [M100002]
Q: Does EPA approve the use of a non-regenerative carbon adsorption
system as the control technology under 40 CFR part 63, subpart MMMM,
for the metal parts coating operations of East Penn Manufacturing in
Lyon Station, Pennsylvania?
A: Yes. EPA approves this request based on the conditions set forth
in this letter, and provided that the request does not relieve East
Penn of any other requirements of MACT subpart MMMM.
Abstract for [M100004]
Q: Does EPA approve alternative operating parameters under 40 CFR
part 63, subpart NNNNN, for the Irgafos V-47 caustic scrubber at the
Ciba Corporation facility in McIntosh, Alabama?
A: No. EPA cannot approve the requested alternatives without
evaluating the performance test data that is collected using these
proposed alternative parameters which needs to be submitted by Ciba
Corporation to demonstrate compliance with the applicable emission
limit set out in Table 1 of MACT subpart NNNNN.
Abstract for [M100005]
Q: Is the polyethylene terephthalate (PET) solid state
polymerization (SSP) process at the DAK Americas facility in Cooper
River, South Carolina, subject to 40 CFR part 63, subpart FFFF?
A: Yes. The SSP process is a miscellaneous organic chemical
manufacturing process unit (MCPU) which manufactures a product, PET,
which is described by the North American Industry Classification System
325. In doing so, it, generates a hazardous air pollutant (HAP),
acetaldehyde. The MCPU is located at a major source of HAP. Thus, the
SSP process satisfies all of the conditions for applicability under
MACT subpart FFFF, specifically 40 CFR 63.2435 (a) and (b)(1) through
(3).
Abstract for [M100006]
Q: Does EPA waive excess emissions reporting requirements under 40
CFR part 63, subpart EEE, for a waste liquid fuel-fired boiler system
(WFBS) at the Diversified Scientific Services facility in Kingston,
Tennessee, if the unit is equipped with an automatic fuel cutoff?
A: No. EPA does not waive the excess emissions reporting
requirements of MACT subpart EEE even when the WFBS has safe guards
that minimizes emissions because there remain numerous reportable
situations involving continuous monitoring system devices, such as
opacity monitors, thermocouples, pressure transducers, and flow meters,
that could malfunction and that should be included in the required
report.
Abstract for [1000004]
Q1: Is the exemption in section 60.14(e)(4) of the General
Provisions applicable to Power Boiler No. 6, at Rayonier Performance
Fibers, in Fernandina Beach, Florida, even though the emission rate of
nitrogen oxide (NOX) will increase, such that it will cause
the boiler to not become subject to NSPS subpart Db, Standards of
Performance for Industrial-Commercial-Institutional Steam Generating?
A1: Yes. Even though there will be an increase in the
NOX emission rate, the operational or physical changes made
at the facility are not considered modifications under 40 CFR 60.14(e)
of the General Provisions. Thus, the changes did not subject the Power
Boiler No. 6 to NSPS subpart Db.
Q2: An interpretation of the reference in 40 CFR 60.14(e)(4) to the
``facility's construction specifications'' is requested for Power
Boiler No. 6. The boiler was purchased by Rayonier as a traveling grate
boiler and was later converted to a bubbling fluidized bed boiler.
A2: The exemption in 40 CFR 60.14(e)(4) relates to the construction
specifications prior to the date a standard becomes applicable to a
source category. Because the applicability date for 40 CFR part 60,
subpart Db, is June 18, 1984, 40 CFR 60.14(e)(4) relates to the
construction specifications for Power Boiler No. 6 prior to that date.
Abstract for [1000007]
Q: Does EPA grant the request of Detroit Edison's River Rouge Power
Plant in River Rouge, Michigan, to eliminate the requirement for
temperature monitors on the gas stream exits of the thermal dryers?
A. No. Continuous temperature monitoring, as required in 40 CFR
60.256(a) (1), indicates compliance status with respect to the carbon
monoxide (CO) limits. The temperature record ensures the source
temperature correlates with the results of performance tests or other
emissions
[[Page 36124]]
tests. Monitoring temperature is essential because improperly tuned
operations at off-design levels decrease combustion efficiency
resulting in increased CO emissions. Additionally, Detroit Edison has
not requested an alternative form of monitoring (see 60 CFR 60.13(i)),
but rather the elimination of the monitoring requirements. EPA is
unable to grant this request because the Region does not have authority
to amend NSPS subpart Y.
Abstract for [1000008]
Q: Does the landfill gas treatment system proposed by the City of
Midland, Michigan, meet the requirements that allow the landfill gas to
be exempt from control requirements per 40 CFR 60.752(b)(2)(iii)(C)
when burned in internal combustion engines? A: Yes. Because the
proposed landfill gas treatment system will use 10-micron filtration
and sufficient dewatering, it meets the current requirements used by
EPA for gas ``treatment'' and is therefore exempt from the requirements
of 40 CFR 60.752(b)(2)(iii)(C).
Abstract for [M100009]
Q: Is dry cleaning equipment that was initially installed prior to
December 21, 2005, but was removed from its original location, sold to
a new owner, and relocated subsequent to December 21, 2005, subject to
the area source, non-residential carbon adsorption requirements at 40
CFR 63.322(o)(2)?
A: Yes. Reselling and relocating dry cleaning equipment constitutes
installation of a dry cleaning system. Therefore dry cleaning equipment
that is resold and relocated would be subject to the secondary carbon
adsorption requirements of 40 CFR 63.322(o)(2).
Abstract for [1000009]
Q: Does EPA approve higher landfill gas temperatures under 40 CFR
60.753(c) for specific extraction and leachate wells at Veolia's
Glacier Ridge Landfill near Horicon, Wisconsin?
A: Yes. Because the proposed operating limit of 148 degrees
Fahrenheit is properly supported by data that shows there would be a
minimal risk of a landfill fire or significantly inhibited anaerobic
decomposition, EPA approves the higher landfill gas temperatures under
40 CFR 60.753(c).
Abstract for [M100010]
Q: Does EPA approve a request to waive the minimum secondary
combustion chamber temperature operating parameter limit under 40 CFR
part 63, subpart EEE, for the Heritage-WTI (WTI) facility in East
Liverpool, Ohio?
A: No. EPA concludes that the rotary kiln and the secondary
combustion chamber (SCC) are separate combustion chambers and thus does
not approve the request under MACT subpart EEE. WTI cannot legitimately
argue that the SCC at its facility does not contain a steady-state, or
near steady-state, process wherein fuel, hazardous waste, and oxidizer
(i.e., pure oxygen or ambient air) feed rates are controlled, since the
SCC is engineered to allow WTI to feed pure oxygen or ambient air into
the SCC to improve combustion. EPA concludes that the SCC is an area in
which controlled flame combustion of hazardous waste occurs. Therefore,
EPA disapproves WTI's request in its original and revised comprehensive
performance test plans to determine that the Rotary Kiln and the SCC
are one combustion chamber and to eliminate the need for a minimum
combustion chamber temperature operating parameter limit.
Abstract for [1000011]
Q: Does 40 CFR part 60, subpart CCCC, apply to the thermal
destruction unit operated by PIKA International in Calhoun County,
Arkansas?
A: Yes. NSPS subpart CCCC applies because the waste that is burned
(1) Is a RCRA solid waste, but not a RCRA hazardous waste; (2) meets
the definition of a commercial solid waste; and (3) is not eligible for
any exemptions under NSPS subpart CCCC. In addition, NSPS subpart CCCC
applies as a result of the date construction began on the incinerator.
Abstract for [M100012]
Q: If Riceland Cabinet's (Riceland) facility in Orville, Ohio,
which is subject to 40 CFR part 63, subpart JJ, relocates its facility
and reduces its emission to area source status thresholds after the
NESHAP compliance date, does it remain subject to the MACT subpart JJ
and Title V Permitting requirements?
A: Yes. The relocated facility would be considered an existing
source under MACT subpart JJ. The relocated facility would also be
required to obtain a Title V Permit. The ``Once In Always In'' Policy
(OIAI Policy) allows new sources the option to comply with federally
enforceable limits after the compliance date in order to not be subject
to the NESHAP. However, a relocated facility cannot be defined as a new
source for the purposes of the NESHAP. To be considered a new source, a
source would have to be constructed after the compliance date; however,
relocating a facility is not construction according to NESHAP
definition of construction. Construction is defined as the on-site
fabrication, erection, or installation of an affected source.
Construction does not include the removal of all equipment comprising
an affected source from an existing location and reinstallation of such
equipment at a new location. Any source that is not a new source is
defined as an existing source.
Abstract for [1000012]
Q: Does EPA approve the use of alternative method ASTM D975-07b for
fuel certification under 40 CFR part 60, subpart Dc, in lieu of ASTM
D396 for Quest Diagnostics in Chantilly, Virginia?
A: Yes. ASTM D975-07b is more stringent than ASTM D396 in all cases
except viscosity, which will not affect sulfur dioxide emissions, and
thus is acceptable under NSPS subpart Dc.
Abstract for [1000013]
Q1: Is Method 7E an allowable alternative test method for measuring
nitrogen oxide (NOx) emissions at nitric acid plants for the purposes
of determining compliance with 40 CFR part 60, subpart G?
A1: No. Method 7E is not approved for use to demonstrate compliance
with NSPS subpart G.
Q2: Is Method 6C an allowable alternative test method for measuring
sulfur dioxide (SO2) emissions at sulfuric acid plants for the purposes
of determining compliance with 40 CFR part 60, subpart H?
A2: No. Method 6C is not approved for use to demonstrate compliance
with NSPS subpart H.
Abstract for [1000015]
Q: Will EPA reconsider its February 8, 2006 determination that 40
CFR part 60, subpart KKKK, applies to a turbine at Great River Energy
in Cambridge, Minnesota?
A: No. The request does not provide any new information that would
cause the Agency to reconsider the February 8, 2006 determination that
NSPS subpart KKKK applies.
Abstract for [1000016]
Q: Did construction commence on the proposed installation of a gas
turbine at Great River Energy (GRE) in Cambridge, Minnesota, before the
applicability date of 40 CFR part 60, subpart KKKK?
A: No. GRE did not begin installation of the turbine nor enter into
a contractual obligation to undertake and complete within a reasonable
time a continuous program of construction for the installation of the
turbine prior to
[[Page 36125]]
the applicability date of 40 CFR part 60, subpart KKKK.
Abstract for [1000017]
Q1: Is the installation of a capacitor bank and tuned reactor at
the electrical substation servicing an electric arc furnace (EAF) at
the Alton Steel, Inc. facility, a physical or operational change to an
existing EAF under 40 CFR 60.14 of the General Provisions?
A1: Yes. The capacitor/reactor project increased the capacity
(i.e., the production rate) of the existing EAF and is therefore an
operational change to the EAF under 40 CFR 60.14, which resulted in a
kilogram per hour increase in the emission rate of particulate matter.
Q2: Is the capacitor/reactor project exempt from the definition of
``modification'' because it is ``routine maintenance, repair, or
replacement'' under 40 CFR 60.14(e)(1)?
A2: No. The capacitor/reactor project was not routine maintenance,
repair, or replacement under 40 CFR 60.14(e)(1).
Q3: Is the capacitor/reactor project not subject to 40 CFR part 60,
subpart AAa because it is not considered ``modification'' based on the
capital expenditure exemption at 40 CFR 60.14(e)(2)?
A3: Yes. The capacitor/reactor project allowed the EAF to increase
the rate of production but involved no capital expenditure on the
``existing facility'' (i.e., the EAF as it is defined at 40 CFR
60.271(a)). All of the monetary expenditure associated with the project
involved replacing components and adding new components to the
electrical substation that supplies power to the EAF. Because the
capital expenditure exemption at 40 CFR 60.14(e)(2) applies, the
capacitor/reactor project has not triggered the applicability of NSPS
subpart AAa.
Abstract for [1000019]
Q1: Does 40 CFR part 60, subpart AAAA, apply to the syngas
gasification process at Fulcrum BioEnergy's (Fulcrum) proposed facility
in McCarran, Nevada?
A1: No. Because Fulcrum's proposed syngas gasification process is
neither combustion nor pyrolysis, the syngas generation unit is not
considered a ``pyrolysis/combustion unit'' or ``municipal waste
combustion unit'' as defined in NSPS subpart AAAA.
Q2: Does 40 CFR part 60, subpart AAAA, apply to the combined cycle
combustion turbine if the facility meets the requirements for the small
power production facility exemption or the cogeneration facility
exemption?
A2: No. 40 CFR 60.1020(b) and (c) list the requirements that a
facility must meet to be exempt from NSPS subpart AAAA as a small power
production facility or cogeneration facility. Those requirements
include meeting criteria established by the Federal Power Act,
combusting homogeneous waste, and providing notification and
documentation to EPA. EPA concurs with Fulcrum's assessment that the
gasified waste would be considered homogeneous. However, to qualify for
either of the facility exemptions Fulcrum would also need to provide
appropriate notification and documentation that it meets the criteria
established by the Federal Power Act.
Q3: Does 40 CFR part 60, subpart AAAA, apply to the air pollution
control flare?
A3: No. As long as the flare is operated solely as an air pollution
control device, it is excluded from the definition of ``municipal waste
combustion unit'' under NSPS subpart AAAA.
Abstract for [M100014]
Q: Does EPA approve NuStar Logistics (``NuStar'') request for
alternative monitoring of emissions under 40 CFR part 63, subpart R, of
continuous presence of a pilot flame for the vapor combustion unit
(VCU) in lieu of temperature monitoring at the firebox at its bulk
gasoline terminal in Colorado Springs, Colorado?
A: EPA does not approved NuStar alternative monitoring request
because it does not demonstrate meeting the requirements of 40 CFR
63.8(f)(4), 63.427(a)(5), and 63.428(c)(3)). Additional information
needs to be provided within 30 calendars days after receipt of this
letter. [Additional information was not provided.]
Abstract for [M100015]
Q: Does EPA approve the request of the Tooele Chemical Agent
Disposal Facility (TOCDF) in Stockton, Utah, to waive the requirement
to establish, and subsequently monitor, at the Deactivation Furnace
System (DFS), a 12-hour rolling average (HRA) feed rate for mercury,
ash, semi- and low-volatile metals, and chlorine required by 40 CFR
63.1290(l), (m), (n), and (o), respectively?
A: EPA conditionally approves TOCDF's request to waive the
requirement to establish, and subsequently monitor, at the DFS, a 12-
HRA feed rate for mercury, ash, semi- and low-volatile metals, and
chlorine required by 40 CFR 63.1290(l), (m), (n), and (o),
respectively. EPA's approval is limited to when burster and fuze pairs
from 4.2'' HD mortars, HT mortars, and minimal amounts of process
generated waste such as agent contaminated rags and small metal parts
are fed to the DFS. Additionally, EPA's approval is based on a feed
rate to the DFS of combined 4.2'' mortar burster/fuze pairs of 274/
hour, as well as the RCRA Permit limits for process generated waste,
and TOCDF's commitment to monitor and comply with those limits.
Abstract for [M100016]
Q: Does EPA approve the request of the Tooele Chemical Agent
Disposal Facility (TOCDF) located in Stockton, Utah, under 40 CFR part
63, subpart EEE, to modify the first condition of the approved
alternative monitoring request (AMR) of April 27, 2006, to also include
munitions processing? The first condition states that ``this approval
shall apply only to the Baseline Processing phase of the TOCDF Mustard
campaign which restricts processing to only those ton containers (TCs)
in which the level of Hg in the liquid phase is less than 1 ppm''?
A: Yes. EPA approves modifying the scope of the AMP request to
include the processing of the above TCs, munitions, and secondary
waste. Based on the information provided, EPA believes that TOCDF can
process the additional TCs, munitions, and secondary waste and maintain
compliance with 40 CFR part 63, subpart EEE standards.
Abstract for [M100017]
Q: Does EPA approve under 40 CFR part 63, subpart EEE, the request
of the Tooele Chemical Agent Disposal Facility (TOCDF) in Stockton,
Utah, to modify Condition 2 of the alternative monitoring
request approved by EPA on June 29, 2009? The condition states among
other things, that during the Non-Baseline Processing Phase, the
sampling period for the Appendix K System sorbent tube trap sets shall
be no greater than 12 hours, and Tooele requests to change ``no greater
than 12 hours'' to ``no greater than 12 hours (plus or minus 30 minutes
to allow for unforeseen events)''?
A: EPA approves the revision to Condition 2 because TOCDF
has confirmed that even though the start or stop time may vary by up to
30 minutes, TOCDF will sample continuously. For those periods where the
start or stop time varies by 15 minutes or more, TOCDF will provide a
reason code in its reporting to explain why sampling was plus or minus
15 minutes or more. In addition, EPA believes the change in Condition
2 is approvable for the reasons expressed in its June 29, 2009
letter.
[[Page 36126]]
Abstract for [M100018]
Q1: Does EPA approve Albemarle Corporation's (Albemarle)
alternative monitoring request for its facility in Orangeburg, South
Carolina, to measure the liquid temperature in the receiver of its
process condensers as described in 40 CFR 63.2460(c)(2)(v) when
conducting the process condenser demonstration required by 40 CFR
63.1257(d)(3)(iii)(B)?
A1: Yes. EPA agrees that measuring the liquid temperature of the
condensed liquid in the receiver would be an acceptable alternative to
measuring the exhaust gas temperature as required by 40 CFR
63.1257(d)(3)(iii)(B) because the temperature of the condensed liquid
and the exhaust gas are in equilibrium.
Q2: Does EPA approve Albemarle's alternative recordkeeping request
under 40 CFR part 63, subpart GGG, to maintain records of standard and
non-standard batch production to allow the calculation of rolling
annual emissions on a daily basis to comply with the daily rolling 365-
day HAP emissions once per month as required by 40 CFR 63.1259(b)(4)?
A2: Yes. For purposes of compliance with the annual mass limits of
40 CFR 63.1254(a)(2) and (b)(2), Albemarle must calculate and record
the daily rolling annual total emissions for the previous month by the
fifth day of each month.
Q3: Does EPA approve Albemarle's request for a waiver of the
performance test requirements of 40 CFR 63.11(b)(6)(i) for a flare used
to control Hydrogen Cyanide (HCN) emissions from the HCN Pharmaceutical
Manufacturing Process Unit (PMPU)?
A3: Yes. EPA approves a waiver of the requirement to conduct a
performance test to demonstrate compliance with 40 CFR 63.11(b)(6)(i).
This waiver is for the same flare being operated under the same
conditions for which Albemarle submitted information in 2002 and 2003
to support its request for a waiver of the performance test
requirements under 40 CFR 60.18(c)(3)(i). In addition, the regulatory
language of 40 CFR.11(b)(6)(i) is identical to that of 40 CFR
60.18(c)(3)(i).
Q4: Does EPA approve Albemarle's setting alternate operating limits
for a hydrochloric acid (HCl) bubbler control device to those required
by 40 CFR 63.1258(b)(1)(ii) for scrubbers?
A4: EPA conditionally approves the alternate operating parameters
pending a successful performance test and other conditions listed in
the EPA response letter.
Abstract for [1000021]
Q: Do the requirements for external floating roof tanks (EFR) in 40
CFR 60.112b(a)(2), the requirements for internal floating roof (IFR)
tanks in 40 CFR 112b(a)(1) apply, or both, apply to EFR tanks which
have been enclosed with a fixed roof located at the TransMontaigne
Operating Company LP facility in Selma, North Carolina?
A: An EFR tank which is enclosed by the installation of a fixed
roof meets the 40 CFR part 60, subpart Kb description of an IFR tank
and is therefore subject to the requirements for IFR tanks. An enclosed
EFR tank is no longer subject to the NSPS subpart Kb requirements for
EFR tanks.
Abstract for [1000022]
Q1: Is a municipal solid waste landfill that already has a design
capacity equal to or greater than 2.5 million megagrams and 2.5 million
cubic meters required under 40 CFR part 60, subpart WWW, to submit an
amended design capacity report upon approval of a further expansion?
A1: No. The facility is not required to do so as it is subject to
the standards 40 CFR 60.752(b), which does not require such reports.
Q2: Is a municipal solid waste landfill that already has a design
capacity equal to or greater than 2.5 million megagrams and 2.5 million
cubic meters required under 40 CFR part 60, subpart WWW, to submit a
notice for a physical or operation change pursuant to 40 CFR 60.7(a)(4)
upon approval of a further expansion?
A2: Yes. Under NSPS subpart WWW, the facility is required to do so
for all modifications that meet the definition of 40 CFR 60.14.
Abstract for [A100001]
Q1: Does the removal of asbestos containing coating materials from
stator bars at a metal recycling facility in Ashtabula, Ohio,
constitute an asbestos conversion process subject to 40 CFR 61.155?
A1: No. 40 CFR 61.155 applies to situations where regulated
asbestos containing material, and asbestos-containing waste material,
is converted to a non-asbestos material. The information provided by
the requestor indicates that stator bars coated with an asbestos
containing resin and wrapped with tape covered by an asbestos
containing tar will be removed from various locations and the bars will
be taken to a recycling operation where the asbestos containing resin
and tar will be removed from the bars. All of the asbestos that is
removed from the stator bars will remain asbestos after it is removed
from the bars. The asbestos material that is removed will be disposed
of in a landfill. Because the asbestos containing material is not
subject to any process or treatment that would convert it to a
nonasbestos material, there is no conversion to a non asbestos material
taking place.
Q2: Are the notification requirements at 40 CFR 61.145 applicable
to the removal of asbestos covered and coated stator bars at the site
where they are removed and at the site where the asbestos is stripped
from the bars?
A2: At each site where the stator bars are removed, if the surface
area (of the bars to be removed) covered with asbestos containing resin
and tar equals or exceeds 160 square feet, then the notification
requirements of 40 CFR 61.145 apply and a notice must be submitted to
the Federal, State or local agency delegated to receive such
notifications. Because the stator bars will be stripped of asbestos at
a site in Ashtabula, Ohio, a copy of each notification for bars removed
outside of Ohio should also be sent to the Ohio Environmental
Protection Agency. No matter where the bars are removed, a notification
must be in place for each batch of stator bars stripped of asbestos
containing materials at the site in Ashtabula, Ohio.
Q3: Which sections of 40 CFR 61.145(c) apply at the site where the
stator bars are removed?
A3: Because the stator bars are not going to be stripped of
asbestos at the site where they are removed, and because the stator
bars are going to be shipped to Ashtabula, Ohio, the bars must be
handled in accordance with the requirements of 40 CFR 61.145(c)(5)(i)
through (iii).
Abstract for [M100019]
Q: With respect to the operating limits for cold core machines
utilizing capture and wet acid scrubbers to control triethylamine (TEA)
emissions at the Indianapolis Casting facility in Indianapolis,
Indiana: When dampers are manually set in a fixed position, does the
exemption from the continuous parameter monitoring system (``CPMS'')
requirement apply only to exempting a CPMS with regard to damper
position or would a fixed damper position exempt the cold core machine
capture system from monitoring the hourly average rate as with respect
to 40 CFR 63.7740(a)?
A: 40 CFR 63.7710(b)(2)(i) contains two different requirements (at
a minimum) for the capture system: level of ventilation draft and
damper position settings. Both types of CPMS are required, but the CPMS
for damper system is not needed if the damper position is manually set
and in a fixed position. Thus, the CPMS exemption referred to in 40 CFR
63.7740(a)(2)
[[Page 36127]]
applies solely to the installation of a CPMS for damper position.
Abstract for [1000023]
Q: Does EPA approve a request for alternate performance testing
under 40 CFR part 60, subpart KKKK, for combustion turbines and direct-
fired heaters being installed as part of a process modification at the
PL Propylene facility in Houston, Texas?
A: Yes. EPA has determined that the stationary combustion turbines
are subject to the requirements of NSPS subpart KKKK, and has approved
the request to conduct one performance test downstream of the selective
catalytic reduction units, and to apply reference method results from
the NOx continuous monitoring system certification for the initial
demonstration of compliance with 40 CFR 60.4320. However, testing must
be conducted using the fuel or combination of fuels that would result
in the highest emissions.
Abstract for [1000024]
Q. Is the proposed Earth Energy oil sand mine and processing
facility in eastern Utah, which will include mining of the naturally
occurring oil sands and extraction of the bitumen from these sands,
subject to 40 CFR part 60, subpart Ja?
A: No. The Earth Energy facility would not be considered a
``petroleum refinery'' and thus is not subject to NSPS subpart Ja.
Abstract for [M100020]
Q1: Does EPA approve the Tooele Army Depot's (TEAD's) request to
establish a limit on the minimum baghouse inlet temperature to replace
the requirement to establish a limit on the maximum baghouse
temperature (40 CFR 63.1209(k)(1)(i)) to assure compliance with the
dioxin and furan limit in 40 CFR 63.1219(a)(1)?
A1: EPA conditionally approves the use of a minimum baghouse inlet
temperature rather than a maximum baghouse inlet temperature during the
Comprehensive Performance Test if the baghouse inlet temperature is
maintain at the required level, as established in the EPA response
letter.
Q2: Does EPA approve TEAD's request to establish a limit on the
maximum afterburner outlet temperature to replace the requirement to
establish a limit on the maximum baghouse inlet temperature (40 CFR
63.1209(n)(1)) to ensure compliance with the semi-volatile and low
volatility metals limits in 40 CFR 63.1219(a)(3) and (4)?
A2: No. EPA cannot approve the request because the temperature
range of the inlet to the baghouse can vary so dramatically.
Q3: Does EPA approve TEAD's request to establish the maximum
potential particulate matter (PM) generation as a limit to replace the
requirement to establish the maximum ash feed rate limit to ensure
compliance with 40 CFR 63.1219(a)(7)?
A3: Yes. EPA conditionally approves the request to establish the
maximum potential particulate matter (PM) generation as a limit to
replace the requirement to establish the maximum ash feed rate limit,
provided that (i) The propellants, explosives and pyrotechnics (PEP)
feed rate will not exceed 56.28 lb/hr and (ii) the PM generation will
not exceed the worst case theoretical maximum based on the PEP feed
rate above.
Abstract for [M100021]
Q1: Does EPA approve of the operator of a secondary aluminum
continuous caster at the Commonwealth Aluminum Concast (Commonwealth)
facility in Uhrichsville, Ohio, weighing the metal by measuring the
volume of the slab produced by the continuous caster even if the method
does not meet the one percent accuracy requirement at 40 CFR
63.1510(e)?
A1: Yes. Although these accuracies do not meet the one percent
accuracy requirement at 40 CFR 63.1510(e), EPA has concluded that on
the basis of the information provided the affected source should be
able to meet the relevant emission standard.
Q2: May the operator record and report on a 24-hour basis the
chlorine injection rate for its in-line fluxers since the chlorine
meter is not accurate to one percent for the 15-minute block time
period intervals specified in the rule at 40 CFR 63.1510(j)?
A2: No. In this instance, available data indicate that the required
one percent accuracy can be achieved on a 16-hour basis. Therefore, EPA
determines that there is no basis for extending the averaging period
beyond 16 hours.
Q3: May the operator test only one of two identical in-line fluxers
to measure particulate matter emissions?
A3: Yes. Because the in-line casters operate in series, the test
plan does not contemplate testing of PM emissions from each fluxer
individually. For the purposes of compliance calculations, however, the
particulate matter is assumed to emit from the tested caster. This
would represent a conservative worst-case assumption, and does not
require the assumption that an equal amount of particulate matter is
emitted from each caster.
Q4: May the operator conduct performance testing for two of the
four aluminum melting furnaces?
A4: Yes. EPA approves the testing of two of a total of four of the
aluminum melting furnaces if these have the same physical dimensions
and capacity, and the operator charges each furnace with the same
materials and the same reactive fluxing agents in the same proportions,
and this will maintain identical work practices. Also, Commonwealth
will perform three test runs for two representative furnaces during a
complete operating cycle, which is defined for purposes of this testing
as the initial metal charging through the final skim, or about 1.5
hours. In addition, each melting furnace (M1 through M4) has the same
physical dimensions and capacity of 233,000 tons, and maximum 21
million Btu/hour heat input natural gas burners. The testing of
emissions from M1 will be representative of emissions from M3, and the
testing of emissions from M2 will be representative of emissions from
M4.
Abstract for [M100022]
Q1: Does EPA approve the revised comprehensive performance test
plan (CPT) and continuous monitoring system (CMS) performance
evaluation test (PET) plan for Sunoco Chemicals, in Haverhill, Ohio,
pursuant to 40 CFR 63.1207(e)(1)(i)(A)?
A1: Yes. EPA approves Sunoco's revised CPT and CMS PET plan under
MACT subpart EEE.
Q2: Does the requirement for a one-time dioxin/furan test apply to
Boiler UC pursuant to 40 CFR 63.1207(b)(3)(ii) and 63.1207(b)(3)(iii)?
A2: EPA concludes that the requirement for a one-time dioxin/furan
test for Boiler UC does not apply until Sunoco resumes generation and
incineration of its two hazardous waste feedstreams.
Q3: Does EPA approve Sunoco's PM DIL requests for Boiler UC?
A3: Yes. EPA approves Sunoco's PN DIL requests for Boiler UC.
Q4: Does EPA approve Sunoco's request to use data from a 2006 DRE
test on Boiler UC as documentation of conformance with the applicable
DRE emission standard for Boiler UC pursuant to 40 CFR 63.1207(c)(2)?
A4: Yes. EPA approves Sunoco's request to use data from a 2006 DRE
test on Boiler UC as documentation of conformance with the applicable
DRE emission standard for Boiler UC.
Q5: Does EPA approve Sunoco's request to use data from a November
[[Page 36128]]
2001 DRE test on Boiler UE as documentation of conformance with the
applicable DRE emission standard for Boiler UE pursuant to 40 CFR
63.1207(c)(2)?
A5: Yes. EPA approves Sunoco's request to use data from a November
2001 DRE test on Boiler UE as documentation of conformance with the
applicable DRE emission standard for Boiler UE pursuant to 40 CFR
63.1207(c)(2).
Q6: Does EPA approve a maximum theoretical emission concentration
request for Boiler UC and Boiler UE pursuant to 40 CFR 63.7(h) and
63.1207(m)?
A6: Yes. EPA approves a maximum theoretical emission concentration
request for Boiler UC and Boiler UE pursuant to 40 CFR 63.7(h) and
63.1207(m).
Abstract for [1000025]
Q1: Are the flow monitoring procedures under 40 CFR part 60,
subpart RRR, an acceptable alternative to the 40 CFR part 60, subpart
NNN, requirements for the distillation operation at Flint Hills'
facility in Saint Paul, Minnesota?
A1: Yes. EPA finds that in this instance the NSPS subpart RRR flow
monitoring procedures are an acceptable alternative to those under NSPS
subpart NNN. The NSPS subpart RRR requirement to monitor diversions
from the control device accomplishes the same result (i.e., providing a
record of when vent streams are not controlled) as the NSPS subpart NNN
requirement to monitor the flow to the control device.
Q2: Does EPA approve the use of certain monitoring, recordkeeping,
and reporting provisions under 40 CFR part 60, subpart RRR, as
alternative monitoring requirements to those under 40 CFR part 60,
subpart NNN, for the Flint Hills' facility in Saint Paul, Minnesota?
A2: Yes. EPA approves the use of the provisions in NSPS subpart RRR
as an alternative means of demonstrating compliance under NSPS subpart
NNN for the specified distillation unit. As conditions of approval, the
facility must comply with the recordkeeping and reporting requirements
for flow indicators in NSPS subpart RRR and must maintain a schematic
diagram for all related affected vent streams, collection system(s),
fuel systems, control devices, and bypass systems as stated in 40 CFR
60.705(s).
Q3: Does EPA approve a waiver of initial performance tests for
certain boilers and heaters at the Flint Hills' facility in Saint Paul,
Minnesota?
A3: Yes. Pursuant to 40 CFR 60.8(b)(4), EPA conditionally approves
the performance test waiver for the boilers and process heaters which
are fired with fuel gas containing a vent stream from the Poly Unit De-
Propanizer (43V-5), Saturates Gas De-Propanizer (43V-19), and Alky Unit
De-Propanizer (35V-2). This waiver is applicable for boilers and
process heaters that meet the definitions of a boiler or process heater
in 40 CFR 60.701. Both the alternative monitoring and the waiver of
performance testing are contingent upon the vent streams being vented
to a fuel gas system and introduced into the flame zone with the
primary fuel.
Q4: Does EPA approve Flint Hills' request for alternate flare
reporting required by 40 CFR 60.665(l)(4), Subpart NNN?
A4: Yes. EPA approves Flint Hills Resources' (FHR's) request to
comply with the reporting requirements on the status of the pilot flame
in 40 CFR 63.654(g)(6)(i)(B) of Subpart RRR in lieu of the flare
requirements in 40 CFR 60.665(l)(4) of Subpart NNN, based on approval
of the AMP request.
Abstract for [M100023]
Q: What is considered a comparable new source under 40 CFR Part 63,
Subpart PPPPP, when determining if reconstruction has occurred under 40
CFR 3.2 of the General Provisions at John Deere's engine testing
facility in Dubuque, Iowa?
A: While the regulations do not define ``comparable new source,''
it is clear within context of the paragraph (see 63.2, reconstruction
definition) that the term stands for ``a newly reconstructed existing
facility.'' EPA has determined that the addition of the new test cells
equipment to a facility, as defined in 40 CFR part 63, Subpart PPPPP,
does not automatically trigger new source MACT requirements, unless the
definition of reconstruction as listed in 40 CFR 63.2 is met. Based on
the information provided, EPA has determined that for the John Deere
Facility the cost of new equipment is not more than 50 percent of the
cost to construct a comparable new facility. Therefore, the definition
of reconstruction would not be met and new source MACT requirements
were not triggered. The percent cost of installation should be
calculated by dividing the cost of new components (i.e., new test cell
equipment) by the cost of a newly reconstructed existing facility
(i.e., cost of existing test cells and existing equipment) to determine
if the cost criterion in the definition of reconstruction at 40 CFR
63.2 is met.
Abstract for [M100024]
Q1: How does the vacatur of the startup, shutdown, and malfunction
(SSM) exemption provisions of 40 CFR part 63, subpart A, impact the
reporting requirements of 40 CFR part 63, subpart RRR?
A1: In general, the SSM vacatur should have no impact on the
reporting requirements in MACT subpart RRR.
Q2: If a monitoring malfunction occurs that does not cause excess
emissions, is it a reportable occurrence?
A2: Yes, all malfunctions are required to be reported regardless of
the resulting emissions.
Abstract for [1000026]
Q: Does EPA approve the request of the Enbridge Energy facility in
Superior, Wisconsin, to perform an internal inspection under 40 CFR
part 60, subpart Kb, on the internal floating roofs (IFR) tanks while
they are in-service and out-of-service?
A: Yes. Enbridge Energy may perform an internal inspection by
visually inspecting the IFR components from the top of the IFR using
inspection procedures that are similar to those found in 40 CFR
63.1063(d)(1) and 40 CFR part 63, subpart WW. The proposed alternative
monitoring procedure, based on 40 CFR part 63, subpart WW, would serve
to satisfy the requirements of 40 CFR 60.113b(a)(4).
Abstract for [Z100001]
Q: Are sour water streams managed in sour water strippers regulated
upstream of the sour water stripper exit under 40 CFR part 61, subpart
FF?
A: Yes. Assuming that the total annual benzene quantity from
facility waste is 10 Mg/year or greater, as provided by 40 CFR
61.342(b), the facility must comply with the requirements of 40 CFR
61.342 (c)-(h). Thus, these requirements would apply to sour water
streams managed upstream of the sour water stripper exit.
Abstract for [M100025]
Q: Does EPA approve the request of Ross Incineration Services in
Grafton, Ohio, for the hazardous waste incinerator operator to use
alternate operating parameters in lieu of flow rate measurements