Recent Posting to the Applicability Determination Index (ADI) Database System of Agency Applicability Determinations, Alternative Monitoring Decisions, and Regulatory Interpretations Pertaining to Standards of Performance for New Stationary Sources, National Emission Standards for Hazardous Air Pollutants, and the Stratospheric Ozone Protection Program, 70383-70392 [E6-20440]
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Federal Register / Vol. 71, No. 232 / Monday, December 4, 2006 / Notices
Dated: November 20, 2006.
Michael S. Hacskaylo,
Administrator.
[FR Doc. E6–20438 Filed 12–1–06; 8:45 am]
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 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.
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ENVIRONMENTAL PROTECTION
AGENCY
[FRL–8250–5]
Recent Posting to the Applicability
Determination Index (ADI) Database
System of Agency Applicability
Determinations, Alternative Monitoring
Decisions, and Regulatory
Interpretations Pertaining to Standards
of Performance for New Stationary
Sources, National Emission Standards
for Hazardous Air Pollutants, and the
Stratospheric Ozone Protection
Program
Environmental Protection
Agency (EPA).
ACTION: Notice of availability.
AGENCY:
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
The General Provisions to the NSPS
in 40 CFR part 60 and 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
broadly termed applicability
determinations. See 40 CFR 60.5 and
61.06. Although the 40 CFR part 63
NESHAP and section 111(d) of the
Clean Air Act (CAA) regulations contain
no specific regulatory provision that
sources may request applicability
determinations, EPA does respond to
written inquiries regarding applicability
for the 40 CFR part 63 and section
111(d) of the CAA programs. The NSPS
and NESHAP also allow sources to seek
permission to use monitoring or
recordkeeping which is different from
the promulgated requirements. See 40
CFR 60.13(i), 61.14(g), 63.8(b)(1), 63.8(f),
and 63.10(f). EPA’s written responses to
these inquiries are broadly termed
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
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Category
Subpart
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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 broadly termed
regulatory interpretations.
EPA currently compiles EPA-issued
NSPS and NESHAP applicability
determinations, alternative monitoring
decisions, and regulatory
interpretations, and posts them on the
Applicability Determination Index (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 and NESHAP.
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 63 such documents added to the ADI
on November 10, 2006. The subject,
author, recipient, date 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.
The following table identifies the
database control number for each
document posted on the ADI database
system on November 10, 2006; 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.
Title
Alternative Fuel Monitoring.
Exemption from TRS Standard for Brown Stock Washer.
Alternative Monitoring for Scrubber.
Fuel Supplier Certification Statements.
Alternative Monitoring Plan for a Catalytic Cracking Unit.
Alternative Monitoring Plan for a Flare.
Alterations to an Electric Arc Furnace.
Alternative Monitoring Plan for Hydrogen Production Facility.
Compliance Test Waiver Request.
Post Vulcanized Rubber-to-Metal Parts Bonding.
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Summary of Headers and Abstracts
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Abstracts
Abstract for [A060001]
Q: Are residential structures that are
demolished as part of a larger project,
such as highway expansion, subject to
the asbestos requirements under 40 CFR
part 61, subpart M?
A: Yes. EPA finds, pursuant to 40 CFR
61.145, that if two or more residences
under the control of the same owner or
operator are part of a larger demolition
project, such as highway expansion,
they are subject to the asbestos
regulation, NESHAP subpart M.
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Title
Common Duct Testing and Acid Rain Program Opt-in.
Firetube Boilers.
Liquid-to-Gas Ratio Operating Parameter Limit.
Use of Previously Conducted Transfer Efficiency Test.
Alternative Monitoring for Scrubber.
Alternative Monitoring Locations and Parameters.
Alternative Monitoring Plan for Hazardous Waste Combustor.
Alternative Monitoring Plan for Dual Purpose Valves.
Landfill Gas Processing System as Treatment.
Landfill Gas Processing System as Treatment.
Landfill Gas Processing System as Treatment.
Landfill Gas Processing System as Treatment.
Landfill Gas Processing System as Treatment.
Temperature Monitors in Gas Turbines.
Liquid Urea Manufacturing Operations.
Demolition under Control of Same Owner or Operator.
Removal of Floor Mastic Using a Mechanical Buffer.
Applicability of 260 Linear Feet Requirement.
Test Method for Spray-applied Acoustical Materials.
Regulated Asbestos Containing Material.
Meaning of Preclude Access and Dripping.
Clarification of Ownership and Co-location.
Metal Building Insulation.
Post Vulcanized Rubber-to-Metal Parts Bonding.
Use of Tetrahydrofuran (THF) as Raw Material.
Nitrile Stripper Column System.
Non-Dedicated Mixing Vessels.
Modification of Nitric Acid Plant.
Tile Dryers.
Coating of Dishwasher Racks.
Commencement of Construction.
Opacity Monitoring Exemption.
Commencement of Construction.
Reporting Frequency Requirements.
Air Classifiers.
Titanium Dioxide Ore Dryers and Product Dryers.
State Monitoring Requirements in Lieu of 40 CFR Part 60.
Alternative Opacity Monitoring.
Modification and Capital Expenditure Calculations.
Modification and Capital Expenditure Calculations.
SIP-mandated Expenditures and Reconstruction.
Once In/Always In Rule.
Dry Spinning Spandex Production Process Units.
Coating of Test Panels Not Used in Final Product.
Alternative Monitoring of Smelt Dissolving Tank Scrubber.
Point of Determination for Group of Coating Lines.
Alternative Monitoring Plan for HCL Scrubber.
Alternative Monitoring Parameters for a Dual Control System.
Clean Condensate Alternative & Creditable Reductions.
Applicability of White Liquor Oxidation System.
Molding and Core Making.
Clean Condensate Alternative & Creditable Reductions.
Benzene Emissions from Exchange Leaks.
Abstract for [A060002]
Q1: Is floor mastic a Category 1
asbestos-containing material under 40
CFR part 61, subpart M?
A1: No. EPA finds that floor mastic is
not a Category 1 asbestos-containing
material under the Asbestos NESHAP.
However, pursuant to 40 CFR 61.141, it
is a Category II asbestos-containing
material.
Q2: Does the use of a mechanical
buffer with an abrasive pad on floor
mastic cause the floor mastic to become
friable, and thus a Regulated AsbestosContaining Material (RACM) under 40
CFR part 61, subpart M?
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A2: Yes. EPA finds that pursuant to
40 CFR 61.141, the use of a mechanical
buffer with an abrasive pad causes floor
mastic to become friable and, thus, it is
considered a RACM under the asbestos
NESHAP.
Abstract for [A060003]
Q: Does the regulatory threshold of
260 linear feet on pipes apply to
caulking and roof flashing materials that
qualify as regulated asbestos-containing
material (RACM) under 40 CFR part 61,
subpart M?
A: No. EPA finds the 260 linear feet
threshold is applicable only to pipes
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Federal Register / Vol. 71, No. 232 / Monday, December 4, 2006 / Notices
moved in a careful way to minimize
asbestos fiber release.
under the asbestos NESHAP. Other
materials, such as caulking or roof
flashing, are subject to the 160 square
foot standard as specified in 40 CFR
61.145.
Abstract for [A060004]
Q1: Has EPA issued guidance
specifically about spray-applied
acoustical materials under 40 CFR part
61, subpart M?
A1: No. EPA has not issued guidance
under the asbestos NESHAP specifically
about spray-applied acoustical
materials.
Q2: Does EPA recommend that the
public assure spray-applied acoustical
materials to contain asbestos without
testing, and, what method(s) should be
used to test these materials under 40
CFR part 61, subpart M?
A2: No. EPA is not recommending
that the public assure spray-applied
acoustical materials to contain asbestos
without testing. In regards to testing
spray-applied acoustical materials,
Polarized Light Microscopy (PLM) is
specified in 40 CFR part 63 as the
approved testing method; however,
Transmission Electron Microscopy
(TLM) is also an acceptable method.
mstockstill on PROD1PC61 with NOTICES
Abstract for [A060005]
Q: Does 40 CFR part 61, subpart M,
require that all asbestos-containing
materials be removed before the
demolition of a facility?
A: No. The asbestos NESHAP does not
require all asbestos-containing materials
to be removed before demolition.
However, all Regulated Asbestos
Containing Material (RACM) must be
removed from a facility being
demolished or renovated before any
activity begins that would break up,
dislodge, or similarly disturb the
material or preclude access to the
material for subsequent removal.
Abstract for [A060006]
Q: Could EPA clarify the meaning of
the words ‘‘preclude access’’ and
‘‘dropping’’ in 40 CFR 61.145(c)(1) and
61.145(c)(6) of the asbestos NESHAP,
subpart M?
A: EPA finds that the use of the term
‘‘preclude access’’ in 40 CFR
61.145(c)(1) of the asbestos NESHAP is
intended to ensure that all Regulated
Asbestos Containing Material (RACM)
expected to be disturbed during the
demolition or renovation is removed
from the facility before any action is
taken that could prevent safe removal of
the RACM during a later phase of the
project. The use of the term ‘‘dropping’’
is intended to prevent RACM from
falling (instead of being ‘‘placed’’) on
the floor and to ensure that RACM is
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11:51 Dec 01, 2006
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Abstract for [M060001]
Q: Does EPA waive the Method 5 test
requirement for a second process vent,
under 40 CFR part 63, subpart MMM, at
the Arkema facility in Riverview,
Michigan?
A: Yes. EPA waives the Method 5 test
because information submitted by the
facility shows that it is impractical to
test the second vent due to short
operating time, low flow rate, and low
pressure drop. Dust emissions will be
drawn through the first vent which will
be tested, and any remaining dust will
be trapped in the vent collection tank or
in the mineral oil scrubbers.
Abstract for [M060002]
Q: Does EPA find that a coating being
applied at the Cooper Tire & Rubber
facility in Findlay, Ohio, that uses the
same methodology, composition, and
function as a rubber-to-metal coating,
but that is bonded during a heating
process not involving the vulcanization
of rubber, is a rubber-to-metal coating
under 40 CFR part 63, subpart MMMM?
A: No. EPA finds that because the
bonding process is not performed
during the vulcanization process, it is
not considered a rubber-to-metal coating
and should not be included in that
category. Instead, the coating is subject
to the general use coating subcategory
emission limit in 40 CFR 63.3890(b)(1).
Abstract for [M060003]
Q1: Can the required emission tests,
under 40 CFR part 63, subpart DDDDD,
be conducted in the common duct for
boilers 1, 2, and 3 at the Dairyland
Power Cooperative Alma Station in
LaCrosse, Wisconsin?
A1: No. 40 CFR 63.7510 requires that
each unit be tested, and the language in
Section II.F of the September 13, 2004
Preamble to the Final Rule reinforces
this requirement. The facility is required
to submit an alternative test procedure
request with appropriate technical
justification, if it wants to conduct
common duct testing. However, testing
in a common duct is considered a minor
change to a test method; thus, EPA
Regions and delegated States may
approve such a request.
Q2: Does EPA find that boilers 1, 2,
and 3 would be exempt from the boiler
MACT, under 40 CFR part 63, subpart
DDDDD, if they opt into the Acid Rain
Program?
A2: No. EPA finds that 40 CFR
63.7491 includes no such exemption. A
source cannot avoid controlling mercury
emissions by agreeing to control sulfur
dioxide and nitrogen oxides.
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70385
Abstract for [M060004]
Q: Does EPA find that the two 250horsepower firetube boilers planned for
installation at Green Bay Packaging in
Green Bay, Wisconsin, should be
regulated within the ‘‘small gaseous fuel
subcategory’’ as defined in MACT
subpart DDDDD, 40 CFR 63.7575, even
if each boiler’s heat input rating at 100
percent efficiency may reach 10.5
million BTU per hour?
A: Yes. EPA finds that these boilers
are regulated within the ‘‘small gaseous
fuel subcategory’’ as that term is defined
in MACT subpart DDDDD, 40 CFR
63.7575. In response to comments, the
Agency agreed to add firetube boilers to
the definition of small liquid fuel and
gaseous fuel subcategories in the final
rule.
Abstract for [M060005]
Q: Does EPA approve a request from
Minnesota Mining & Manufacturing
Company (3M), under 40 CFR part 63,
subpart EEE, to establish a high energy
wet scrubber’s hydrogen chloride/
chlorine liquid-to-gas ratio operating
parameter limit for a hazardous waste
incinerator unit that is equal to 20.4
gallons per 1,000 dry standard cubic feet
based upon the data from 3M’s
September 1 and 2, 2004,
comprehensive performance test and
not upon the data from 3M’s July 2001,
Resource Conservation and Recovery
Act Trial Burn?
A: No. EPA does not approve the
request because the company has not
demonstrated that the proposed
hydrogen chloride/chlorine liquid-togas ratio operating parameter limit also
corresponds to compliance with the
particulate matter, semi-volatile metal,
and low volatile metals emission
standards.
Abstract for [M060006]
Q: Does EPA approve at the General
Motors (GM) Orion Assembly Plant in
Orion, Michigan, the use of the results
of a transfer efficiency test conducted in
December 2004 for the primer surfacer
and topcoat operations in lieu of
performing another transfer efficiency
test, under 40 CFR part 63, subpart IIII?
A: Yes. EPA approves the use of the
December 2004 test results for the
primer surfacer and the topcoat
operations in lieu of performing an
initial test to determine transfer
efficiency. The test meets the
requirements of MACT subpart IIII, 40
CFR 63.3160(c). There have been no
process or equipment changes since the
test that would trigger retesting, and the
required operating parameters and
transfer efficiency were established
during the test.
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Q: Does EPA approve the continuous
monitoring of fan amps and total
scrubbing liquid flow rate as an
alternative to the scrubber monitoring
parameters required by NSPS Subpart
BB and NESHAP Subpart MM, at the
Weyerhaeuser Company facility in
Bennettsville, South Carolina?
A: Yes. EPA approves this alternative
continuous monitoring plan under
MACT subpart MM and NSPS subpart
BB because the dynamic scrubber
operates near atmospheric pressure and
the proposed monitoring is an
acceptable alternative. Consistent with
the requirements of 40 CFR 63.864, fan
amps and scrubber liquid flow rate must
be monitored at least once each
successive 15-minute period, and
continuous compliance must be
determined based on a 3-hour average.
alternative for the coal mill baghouse
only.
Q3: Does EPA also approve the
request for an alternative to calculate
the minimum combustion chamber
temperature limit as required by 40 CFR
63.1209(j)(1) and (k)(2)?
A3: No. EPA does not approve the
request to set the minimum combustion
chamber temperature as the average of
the highest hourly rolling averages
measured in each trial run burn.
However, EPA finds the source could
establish a minimum combustion
chamber temperature by matching the
combustion chamber temperature
profile during the comprehensive
performance test using the specific
procedures described in EPA’s response
as an alternative to establishing the
minimum combustion chamber
temperature.
Abstract for [M060008]
Abstract for [M060009]
Q1: Does EPA approve the request for
an alternative monitoring location to
continuously monitor total
hydrocarbons and carbon monoxide,
under 40 CFR part 63, subpart EEE, at
the Ash Grove Cement Company facility
in Overland Park, Kansas?
A1: Yes. EPA approves the request to
monitor hydrocarbons in the by-pass
and between stages numbers 2 and 3 of
the preheater instead of in the main
stack, pursuant to MACT subpart EEE,
40 CFR 63.1209(g)(1) and 63.8(f). Both
the bypass and preheater gas streams
must have a hydrocarbon limit of 10
ppmv on an hourly rolling average basis
as defined in MACT subpart EEE. The
location of the hydrocarbon monitors
must be as specified in the
Comprehensive Performance Test Plan,
downstream of the bypass baghouse,
while the preheater monitor shall be
located in the gas stream between stages
numbers 2 and 3 of the pre-heater in a
manner that ensures a representative
sample of gas will be monitored.
Q2: Does EPA also approve the
request for an alternative method to
calculate the maximum gas temperature
at the inlet to the facility’s particulate
matter control device, under 40 CFR
part 63, subpart EEE?
A2: Yes. EPA approves this request
for an alternative calculation pursuant
to MACT subpart EEE, 40 CFR
63.1209(g)(1) and 63.8(f) due to the
potential danger associated with
operating the coal mill baghouse at an
elevated temperature. The facility will
establish that the maximum gas
temperature at the inlet of the coal mill
baghouse does not exceed 200 degrees
Fahrenheit. Establishing the maximum
gas temperature at the inlet is an
Q: Does EPA approve the alternative
monitoring request to continuously
monitor oxygen and temperature instead
of carbon monoxide or total
hydrocarbons, under 40 CFR part 63,
subpart EEE, at the Holcim facility in
Clarksville, Montana?
A: Yes. EPA approves this alternative
monitoring request pursuant to MACT
subpart EEE, 40 CFR 63.1209(g)(1) and
63.8(f), provided the facility meets the
conditions established for the
performance test for destruction and
removal efficiency (DRE) that
demonstrates compliance with the DRE
standard found in 40 CFR 63.1204(c),
and carbon monoxide and total
hydrocarbon standards found in 40 CFR
63.1204(a)(5), as indicated in EPA’s
response.
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Abstract for [M060007]
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11:51 Dec 01, 2006
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Abstract for [M060010]
Q: Could EPA clarify the relationship
between ownership and co-location in
regards to the applicability of 40 CFR
part 63, subpart HH, to the Mocane
Cryogenic/Compressor Station located
near Forgan, Oklahoma, and owned by
Regency Gas Services and Colorado
Interstate Gas?
A: EPA finds that all the facility
operations are located at a single site, as
defined in 40 CFR 63.761 of MACT
subpart HH, and, because the
transmission and storage source
category begins where natural gas enters
the transmission pipeline, the site is
subject to MACT subpart HH. EPA also
finds the equipment qualifies as a single
Title V source with all equipment
subject to Title V permitting. Because of
separate ownership, individual Title V
permits will be issued to the owner of
the specific equipment.
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Abstract for [M060011]
Q: Does 40 CFR part 63, subpart NNN,
apply to the metal building insulation
produced at CertainTeed’s facility in
Kansas City, Kansas?
A: Yes. EPA finds that metal building
insulation meets the definition of
building insulation for purposes of
MACT subpart NNN, and that
production of this insulation at the
CertainTeed facility is subject to MACT
subpart NNN.
Abstract for [M060012]
Q: Does EPA find that an autoclave
should be included in the rubber-tometal or general use subcategory, under
40 CFR part 63, subpart MMMM, if a
partial vulcanization occurs in the first
heating step and the part is submitted
fully vulcanized in the autoclave, as is
the case of the Cooper Standard
Automotive facility in Michigan?
A: EPA finds that the autoclave
should be included in the rubber-tometal subcategory under MACT subpart
MMMM. EPA has determined that the
second coating step of a metal insert
bonded to rubber does involve
vulcanization based on the stress test
results done on two metal parts coated
with the same adhesive, and should be
included in such subcategory.
Abstract for [M060013]
Q: Does EPA find that the substantive
control, testing, and monitoring
requirements of 40 CFR part 63, subpart
PPP, apply to the 3M process using
tetrahydrofuran (THF) as a raw material
at the Specialty Material Manufacturing
facility in Cottage Grove, Minnesota?
A: Yes. EPA finds that the language at
40 CFR 63.1420(d)(3) only exempts
those processes which produce
polyether polyols from epoxide
polymerization, and, by its terms, does
not extend the exemption under MACT
subpart PPP to processes which produce
polyether polyols from THF. The facility
did not provide the Agency sufficient
information to determine whether only
the recordkeeping or demonstration
requirements at 40 CFR 63.1420(b)(1)
would apply to the process.
Abstract for [M060014]
Q1: Does EPA find that the nitrile
stripper column (NSC) system at the
INVISTA S.a.r.l. (INVISTA) Victoria
plant should be classified as a waste
management unit or a recovery device,
under 40 CFR part 63, subpart PPP, or
can it be subject to two sets of
requirements at the same time because
it may qualify both as a waste
management and a recovery device
under the Hazardous Organic National
Emissions Standard for Hazardous Air
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Pollutants (HON) rule, 40 CFR part 63,
subpart F?
A1: EPA finds that the NSC system
cannot be subject to two sets of
standards under the HON rule and that
it should be classified as a waste
management unit under that rule. Based
on the concept of ‘‘discarded’’ within
the terms ‘‘point of determination’’ and
‘‘wastewater’’ in the HON rule, the NSC
system must either be a recovery device
within the CMPU or a waste
management unit outside of the CMPU.
The fact that the NSC system is
receiving the stormwater stream from
the Victoria plant, in addition to the
stream from the ADN unit for which it
was originally designed, clarifies for the
Agency that the NSC system is outside
of the CMPU. The liquid stream
transferred from the ADN process to the
NSC system is, therefore, ‘‘discharged’’
to the NSC system. This makes the NSC
system a ‘‘waste management unit’’ and
the ADN stream ‘‘wastewater’’, subject
to the performance standards of 40 CFR
63.138 of the HON rule.
Q2: What is the appropriate
classification for the NSC system if the
stormwater runoff is no longer routed to
the ADN unit?
A2: When the stormwater runoff is
removed from the NSC system, the NSC
system should be evaluated as a
recovery device because the NSC system
potentially serves the purpose of
recovering chemicals for fuel value, use,
reuse or for sale for fuel value, use or
reuse.
Abstract for [M060015]
Q: Could EPA clarify the applicability
of the Miscellaneous Organic Chemical
Manufacturing NESHAP (MON rule)
and the Miscellaneous Coating
Manufacturing NESHAP (MCM rule),
under 40 CFR part 63, subparts FFFF
and HHHHH respectively, to nondedicated mixing vessels which support
coatings manufacturing in three
different areas at the Cytec Industries
facility in Havre de Grace, Maryland?
A: EPA determines that in area one
the non-dedicated HAP mixing vessels
are used in the production of ‘‘prereact’’ isolated intermediates which are
stored below ambient temperature until
further processing to produce a coating
occurs, and therefore, are subject to the
MON. The pre-react is similar to a
synthesis operation producing a MON
chemical described by SIC code 289,
rather than a coating. EPA agrees that
since the ‘‘pre-react’’ meets all of the
criteria specified in EPA’s response, it is
a MON product and therefore the
mixing vessel that produces it is subject
to the MON. In area two, the MON
chemical is mixed with curing systems,
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fillers, and other additives, and a
coating is produced. Since the non
dedicated HAP mixing vessels in area
two are associated with the production
of a coating, they are part of the
miscellaneous coating manufacturing
subject to the MCM rule. Area three
consists of the application of the coating
produced in area two. Neither the MON
nor the MCM apply to the application
of coatings.
Abstract for [M060016]
Q: Does MACT subpart G, pursuant to
40 CFR 63.100(b)(4), provide minor
source status to International Specialty
Products’ butanediol facility in Lima,
Ohio, given that the facility is no longer
part of the BP Amoco Chemical
Company (BP) major source; has actual
emissions of less than 2 tpy of
individual hazardous air pollutants
(HAP) and less than 4 tpy of total HAP;
shares no common control or ownership
with BP; and is a discrete facility that
is not contiguous with any BP property
or any of the remaining sources listed
on the current BP Title V permit?
A: No. EPA finds that the facility is
not eligible for minor source status
under MACT subpart G. It was
constructed and permitted as a major
source on the compliance date for new
sources in the HON. Thus, according to
the ‘‘once in, always in’’ policy, it
remains subject to the HON rule, even
if it subsequently reduces its emissions
below major source thresholds.
Abstract for [M060017]
Q: Does 40 CFR part 63, subpart YY,
apply to the spandex production
equipment at the Invista facility in
Waynesboro, Virginia, where the
equipment is part of one or more dry
spinning spandex production process
units?
A: No. EPA finds that the spandex
production equipment is not subject to
MACT subpart YY. 40 CFR
63.1103(h)(1)(ii) defines emission
points, listed in paragraphs (h)(1)(i)(A)
through (C), that are associated with a
dry spinning spandex production
process unit that are not subject to the
requirements of 40 CFR 63.1103(h)(3)
even though the process is part of the
spandex production source category.
Abstract for [M060018]
Q: Does 40 CFR part 63, subpart
MMMM, apply to a spray booth at the
PPG Industries, Inc. (PPG) facility in
Springdale, Pennsylvania, that would be
used to prepare painted sample panels
to be tested at a laboratory?
A: No. EPA determines that PPG’s
proposed new spray booth would not be
subject to NESHAP subpart MMMM, the
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Surface Coating of Miscellaneous Metal
Parts and Products rule, since the spray
booth would not be used to apply
surface coating of ‘‘miscellaneous metal
parts or products,’’ which include
certain various ‘‘industrial, household,
and consumer products,’’ or their
‘‘metal components,’’ i.e., parts, as
defined in 40 CFR 63.3881. The sample
panels that PPG plans to prepare in its
new spray booth do not qualify as
‘‘industrial, household, and consumer
products’’ because they will be prepared
solely to allow coatings to be tested in
a laboratory, will not be sold in
commerce, and will eventually be
recycled as scrap metal. The sample
panels also do not qualify as ‘‘metal
components’’ of ‘‘industrial, household,
and consumer products’’ because the
panels will never become part of an
industrial, household, or consumer
product.
Abstract for [M060019]
Q: Does EPA approve continuous
monitoring of fan amperage and
scrubbing liquid flow rate in lieu of
scrubber pressure drop under 40 CFR
part 63, subpart MM, for the smelt
dissolving tank scrubber at the SmurfitStone Container Hopewell Mill in
Hopewell, Virginia?
A: Yes. EPA finds that pressure drop
is not the best indicator of control
device performance for low-energy
entrainment scrubbers. Compliance
with MACT subpart MM could be
demonstrated by verifying ID fan
operation, maintaining a scrubber liquid
flow rate, and maintaining a scrubbing
liquid supply pressure based on
established parameters from the
facility’s performance test.
Abstract for [M060020]
Q: Does EPA agree that the Point of
Determination (POD) for the
predominant use ratio (e.g., 90 percent/
10 percent) which, according to 40 CFR
63.4281(e), would determine whether
part 63, subpart OOOO (‘‘Fabric
NESHAP’’) or subpart JJJJ (‘‘Paper and
Other Web Coating NESHAP, POWC
NESHAP’’) would apply, can be located
at the entry point to the common control
device for the Cytec Engineered
Materials Inc. facility in Havre de Grace,
Maryland?
A: No. EPA does not approve Cytec’s
request to consider the entry point to
the common control device for the four
coaters/dryers as a POD for purposes of
establishing the MACT subpart OOOO
predominant use ratio. 40 CFR
63.4281(e) states that ‘‘any web coating
line must comply with the subpart of
this part that applies to the predominant
use activity conducted at the affected
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source.’’ This indicates that a
predominant use determination under
the Fabric NESHAP can be made only
with respect to a single coating line, not
groups of coating lines. Therefore,
Cytec, Inc. must assure ensure that its
three coaters/dryers subject to POWC
NESHAP comply with all of the POWC
NESHAP’s requirements, and that its
one coater/dryer subject to the Fabric
NESHAP complies with all of the Fabric
NESHAP’s requirements.
Abstract for [M060021]
Q: Does EPA approve, under 40 CFR
part 63, subpart NNNNN, the
monitoring of alternative operating limit
parameters (scrubber base temperature
and indicators of proper liquid flow) at
the DuPont Washington Works facility
in Washington, West Virginia?
A: Yes. EPA finds that DuPont has
demonstrated that the scrubber
monitoring specified under MACT
subpart NNNNN is not appropriate for
its process, and that the proposed
alternative monitoring meets the
requirements for approval in 40 CFR
63.9025(b) and 63.8(f).
in EPA’s response. The data would be
generally considered creditable if it
demonstrates that such emission
reductions resulted from efficiency
improvements to a control device that
can be verified; are clearly from
additional improvements in technology;
and are not otherwise needed to meet
regulatory requirements.
Abstract for [M060024]
Q: Does EPA find that the White
Liquor Oxidation (WLOx) system
portion of a pulp and paper mill’s
oxygen delignification system subject to
the requirements of the Pulp and Paper
MACT, 40 CFR part 63, subpart S, at the
Palatka Mill in Palatka, Florida?
A: No. EPA finds that the WLOx
system is not named as one of the pieces
of process equipment in the regulatory
definition of an oxygen delignification
system and therefore is not subject to
the MACT subpart S requirements in 40
CFR 63.443.
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Abstract for [M060022]
Q: Does EPA approve monitoring the
secondary power from the electrostatic
precipitator (ESP) as an alternative
monitoring parameter to monitoring
pressure drop on the scrubber, under 40
CFR part 63, subpart S, for a dualcontrol device consisting of an ESP
followed by a packed tower scrubber at
the International Paper Georgetown
Mill, in Georgetown, South Carolina?
A: No. EPA does not approve
monitoring secondary power from the
ESP in-lieu-of monitoring the pressure
drop on the scrubber because there is no
demonstration to show that the negative
electric charge on particles exiting the
ESP will have anything more than
negligible effects on the efficiency of the
scrubber.
Abstract for [M060025]
Q: Does EPA find that mold and core
making lines that use the ‘‘Expandable
Pattern Casting’’ (or ‘‘Lost Foam’’)
process at the Mueller Company’s
facility in Albertville, Alabama subject
to the MACT requirements for Iron and
Steel Foundries under 40 CFR part 63,
subpart EEEEE?
A: Yes. The pouring, cooling, and
shakeout operations of Mueller’s
Expendable Pattern Casting process are
not significantly different than a
conventional sand casting operation,
and therefore should be considered as
such for 40 CFR part 63, subpart EEEEE
purposes. In addition, Mueller’s pouring
operations would be classified as
pouring stations, not pouring areas. The
main distinctions between a pouring
station and a pouring area are that
pouring stations are automated and that
the pouring can reasonably be assumed
to occur at distinct points.
Abstract for [M060023]
Q: Does EPA approve that emission
reductions achieved as a result of
upgrades to a wastewater lagoon at the
Buckeye facility in Perry, Florida, are
creditable to demonstrate compliance
with the condensate collection
requirements in 40 CFR 63.446(c) of the
Pulp and Paper MACT, 40 CFR part 63,
subpart S?
A: EPA determines that the reductions
may be creditable provided that
Buckeye can provide the necessary data
to satisfactorily demonstrate continuous
compliance with the lb/ODTP
compliance option for condensate
collection and treatment, beginning at
the initial compliance date, as described
Abstract for [M060026]
Q: Does EPA approve that emission
reductions resulting from improvements
to the pulp washer line fans, under 40
CFR part 63, subpart S, creditable for
the Pulp & Paper MACT Clean
Condensate Alternative (CCA) at the
Smurfit-Stone facility in Fernandina
Beach, Florida?
A: No. Generally, a mill can make
efficiency improvements to a control
device and then use the incremental
improvements for CCA credit if the
emission changes are verifiable and
clearly from additional improvements in
technology. The modifications
described for this facility are not
additional improvements in technology,
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but rather equipment upgrades to meet
proper operating levels and result in
HAP reductions from emissions that
should never have been emitted.
Abstract for [Z060001]
Q: Does EPA approve an alternative
monitoring plan for pressure/vacuum
relief valves, under 40 CFR part 61,
subpart FF, for the wastewater treatment
plant tanks and oil-water separator at
the Flint Hills Resources refinery in
Saint Paul, Minnesota?
A: Yes. EPA concludes that the
pressure/vacuum relief valves function
as both pressure relief devices and
dilution air openings. Further, the
Agency recognizes that the requirements
of 40 CFR 61.343(a)(1)(i)(B) and (C) do
not account for this dichotomy, and it
approves the proposed alternative
monitoring plan under NESHAP subpart
FF to resolve the conflicting
requirements.
Abstract for [0600001]
Q: Does EPA approve an alternative
monitoring plan altering the required
daily monitoring, under 40 CFR part 60,
subpart Dc, 40 CFR 60.48c(g), to a
monthly monitoring schedule for
natural gas fuel usage at the Ypsilanti
Community Utilities Authority facility
in Ypsilanti, Michigan?
A: Yes. EPA conditionally approves
the alternative monitoring request to
record natural gas usage for two new
boilers on a monthly, rather than a daily
basis. EPA finds that compliance with
NSPS Subpart Dc can be adequately
verified by keeping fuel usage records
on a monthly basis if only natural gas
is burned. The facility must also specify
how the total fuel usage will be
apportioned to individual boilers.
Abstract for [0600002]
Q: Does EPA approve an exemption
from the Total Reduced Sulfur (TRS)
standard in NSPS subpart BB, 40 CFR
60.283(a)(1)(iv), for the brown stock
washer (BSW) system at the Buckeye
Florida Limited Partnership facility in
Perry, Florida?
A: Yes. Based on cost information
supplied and recent cost estimates from
other facilities, EPA finds that the BSW
system qualifies for a temporary
exemption under NSPS subpart BB.
Should future changes make the control
of TRS emissions from the Number 2
Mill BSW system cost effective, this
exemption will no longer apply, and it
will be necessary for Buckeye to control
TRS emissions.
Abstract for [0600003]
Q: Does EPA approve the continuous
monitoring of fan amps and the total
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scrubbing liquid flow rate as an
alternative to the scrubber monitoring
parameters required by 40 CFR part 60,
subpart BB, and 40 CFR part 63, subpart
MM, for a smelt dissolving tank
dynamic scrubber at the Weyerhaeuser
Company facility in Bennettsville,
South Carolina?
A: Yes. EPA approves these
alternative monitoring parameters. The
dynamic scrubber operates near
atmospheric pressure and thus the
proposed monitoring, in combination
with monitoring of scrubber liquid flow
rate, is an acceptable alternative to the
NESHAP subpart MM requirement to
monitor the pressure loss of the gas
stream and the scrubbing liquid flow
rate. In addition, EPA approves the
request to monitor scrubbing liquid flow
rate as an alternative to the NSPS
subpart BB requirement to monitor
scrubber liquid supply pressure.
Abstract for [0600004]
Q: Does EPA exempt facilities which
use very low sulfur oil from the
requirement to obtain certifications of
sulfur content for each shipment of fuel
oil delivered, under 40 CFR part 60,
subparts Db and Dc, and permit them to
provide only receipts indicating the
type of fuel delivered?
A: No. EPA does not exempt facilities
from the requirement to obtain
certifications of sulfur content for
shipments of fuel oil. The requirements
of NSPS subparts Db and Dc regarding
certification of fuel sulfur content must
be met.
mstockstill on PROD1PC61 with NOTICES
Abstract for [0600006]
Q: Does EPA approve a request for an
exemption from the requirement in
NSPS subpart J, 40 CFR 60.105(a)(2)(ii),
to install, calibrate, operate, and
maintain a carbon monoxide continuous
emission monitor with a 1,000-ppmv
span gas for a fluid catalytic cracking
unit at the Flint Hills Resources facility
in Saint Paul, Minnesota?
A: Yes. EPA finds that the facility
qualifies for the exemption set forth in
40 CFR 60.105(a)(2)(ii) because the
company has met the following
requirements: calibrated a CO CEM with
a span value of 100 parts per million by
volume, dry basis (PPMVD);
demonstrated that the relative accuracy
is 10 percent of the average CO
emissions or 5 PPM CO, whichever is
greater; and demonstrated that the
average CO emissions during a 30-day
period are less than 50 PPMVD with the
CO CEM. The facility still must comply
with a state air permit requirement to
install and maintain a CO CEM with a
100 PPMV span.
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Abstract for [0600007]
Q: Does EPA approve an alternative
monitoring plan for a zinc thermal
oxidizer flare used during periods of
maintenance or malfunction of a vapor
recovery unit at a gasoline loading rack,
under 40 CFR part 60, subpart J, at the
Flint Hills Resources facility in Saint
Paul, Minnesota?
A: Yes. EPA finds that the company
has demonstrated that this refinery fuel
gas meets the criteria in EPA’s guidance
for refinery fuel gas stream alternative
monitoring plans and approves the
alternative monitoring plan.
Abstract for [0600008]
Q1: Does EPA find that the alterations
made in 1985 to electric arc furnace
(EAF) number 2 at Oregon Steel Mill’s
facility in Portland, Oregon, meet the
definition of ‘‘modification’’ under 40
CFR part 60, subpart AAa?
A1: No. Based on the information
provided, EPA finds that the alterations
made in 1985 to EAF number 2 do not
constitute a modification under NSPS
subpart AAa. Although the alterations
increased the production rate of steel
from 25 tons per hour to 50 tons per
hour, they did not increase particulate
matter emissions.
Q2: Does EPA find that the alterations
meet the definition of ‘‘reconstruction’’
under 40 CFR part 60, subpart AAa?
A2: No. Based on the information
provided, EPA finds that the changes
made in 1985 to EAF number 2 do not
constitute a reconstruction under NSPS
subpart AAa. Reconstruction is based on
a comparison of the fixed capital cost of
the new components and a comparable
entirely new facility, that is, a new
eccentric bottom tap EAF capable of
producing 50 tons of steel per hour. The
EAF consists of the furnace shell and
roof and the transformer. The cost of the
1985 alterations was 31.8 percent of the
cost of the comparable entirely new
facility, which is less than the 50
percent reconstruction cost threshold.
Q3: Does EPA find that the other
changes made to the EAF number that
resulted in an increase on the potential
emission rate was accomplished with a
‘‘capital expenditure’’ as defined under
40 CFR part 60, subpart AAa?
A3: No. EPA finds that the changes
made in 1987, 1990, 1991, 1993, 1997
and 1998 to EAF number 2 did not
require capital expenditures as defined
in 40 CFR 60.2. The annual asset
guideline repair allowance percentage
for an EAF is 18 percent. The changes
that enabled increases in production
rate included the purchase of a
transformer and the installation of oxyfuel burners, a post combustion system,
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aluminum current arms, and other
changes, all of which did not cost more
than 18 percent of the basis for an EAF.
Abstract for [0600009]
Q: Does EPA find that the gas
processing system at the Bethel Landfill
in Hampton, Virginia, qualifies as
treatment under NSPS subpart WWW,
pursuant to 40 CFR 60.752(b)(2)(iii)(C)?
A: Yes. EPA considers compression,
filtration, and moisture removal from a
landfill gas for use in eight reciprocating
internal combustion engines to be
treatment pursuant to 40 CFR
60.752(b)(2)(iii)(C). Because the engines
will be exempt from monitoring, they do
not have to be included in the Startup,
Shutdown, and Malfunction Plan (SSM
Plan) required by 40 CFR part 63,
subpart AAAA. However, the treatment
system supplying gas to the turbines
will have to be included in the SSM
Plan.
Abstract for [0600010]
Q: Does EPA consider the gas
processing system that includes the
three turbines at the Grand Central
Landfill in Pen Argyl, Pennsylvania, to
be treatment under 40 CFR part 60,
subpart WWW, pursuant to 40 CFR
60.752(b)(2)(iii)(C)?
A: Yes. EPA considers compression,
filtration, and moisture removal from a
landfill gas for use in an energy recovery
device to be treatment under NSPS
subpart WWW, pursuant to 40 CFR
60.752(b)(2)(iii)(C). Because the engines
will be exempt from monitoring, they do
not have to be included in the Startup,
Shutdown, and Malfunction Plan (SSM
Plan) required by 40 CFR part 63,
subpart AAAA. However, the treatment
system supplying gas to the turbines
will have to be included in the SSM
Plan. Also, Pennsylvania may include
state enforceable requirements in any
permit it issues, based on its review of
state laws and regulations.
Abstract for [0600011]
Q: Does EPA consider the gas
processing system at Keystone Potato
Products’ facility in Hegins,
Pennsylvania, to be treatment under 40
CFR part 60, subpart WWW?
A: Yes. EPA considers compression,
filtration, and moisture removal from a
landfill gas for use in an energy recovery
device to be treatment under NSPS
subpart WWW, pursuant to 40 CFR
60.752(b)(2)(iii)(C). Because the engines
will be exempt from monitoring, they do
not have to be included in the Startup,
Shutdown, and Malfunction Plan (SSM
Plan) required by 40 CFR Part 63,
subpart AAAA. However, the treatment
system supplying gas to the turbines
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will have to be included in the SSM
Plan. Also, Pennsylvania may include
state enforceable requirements in any
permit it issues, based on its review of
state laws and regulations.
Abstract for [0600012]
Q: Does EPA consider the gas
processing system at the Lake View
Landfill in Philadelphia, Pennsylvania,
to be treatment under 40 CFR part 60,
subpart WWW?
A: Yes. EPA considers compression,
filtration, and moisture removal from a
landfill gas for use in an energy recovery
device to be treatment under NSPS
subpart WWW, pursuant to 40 CFR
60.752(b)(2)(iii)(C). Because the engines
will be exempt from monitoring, they do
not have to be included in the Startup,
Shutdown, and Malfunction Plan (SSM
Plan) required by 40 CFR Part 63,
subpart AAAA. However, the treatment
system supplying gas to the turbines
will have to be included in the SSM
Plan.
Abstract for [0600013]
Q: Does EPA consider gas processing
system to be treatment as specified
under 40 CFR part 60, subpart WWW at
the Modern Landfill facility in York,
Pennsylvania?
A: Yes. EPA considers compression,
filtration, and moisture removal from a
landfill gas for use in an energy recovery
device to be treatment under NSPS
subpart WWW, pursuant to 40 CFR
60.752(b)(2)(iii)(C). Because the engines
will be exempt from monitoring, they do
not have to be included in the Startup,
Shutdown, and Malfunction Plan (SSM
Plan) required by 40 CFR Part 63,
subpart AAAA. However, the treatment
system supplying gas to the turbines
will have to be included in the SSM
Plan.
mstockstill on PROD1PC61 with NOTICES
Abstract for [0600014]
Q: Does EPA approve the use of postcombustion chamber temperature
monitors as an alternative to
combustion chamber temperature
monitors in turbines at the Pottstown
Landfill facility in Pottstown,
Pennsylvania, required by 40 CFR part
60, subpart WWW?
A: Yes. EPA has determined that the
location of the temperature monitors on
these turbines is acceptable as an
alternative to being located in the
combustion zone of the turbines.
Abstract for [0600015]
Q: Does 40 CFR part 60, subpart VV,
apply to liquid urea manufacturing
operations?
A: EPA has not provided a sitespecific determination in this case
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because the source has not been
identified. Additionally, EPA is not
prepared to issue a blanket exemption
for liquid urea manufacturing
operations as none was issued during
the rulemaking process. In addition, a
liquid urea facility must look to the
same criteria in 40 CFR 60.480(a) and
(b) as other manufacturers of listed
chemicals to determine whether it is
subject to NSPS subpart VV. The facility
must then consider whether it might be
exempted under 40 CFR 60.480(d).
Abstract for [0600016]
Q: Will plant changes to increase
production capacity result in a
modification of the C–1 Nitric Acid
Plant located at the PCS Nitrogen
Fertilizer facility in Augusta, Georgia? Is
the use of pre-change and post-change
emission testing the appropriate means
of determining whether the change
results in an increase in the NOX
emission rate that will trigger the
finding of a modification?
A: Yes. EPA finds that the plant
changes do constitute a modification
under the NSPS, and the unit would
become subject to NSPS subpart G. EPA
also finds that the manner in which the
Masar emission control system has been
operated in the past and its improper
maintenance makes it impossible to
establish rational pre-change test
conditions for purposes of determining
whether the plant changes will cause an
increase in NOX emission rate. In this
case, emission factors are the most
appropriate method to determine if an
emission increase occurs, and the
appropriate factors show that the
increase in nitric acid production
capacity will result in an emission
increase. Thus, the plan will be subject
to NSPS subpart G requirements
following the proposed production rate
increase.
Abstract for [0600017]
Q: Does 40 CFR part 60, subpart UUU,
apply to a tile dryer at the Florim USA
facility in Clarksville, Tennessee, that
dries formed tiles by convection?
A: No. EPA finds that the tile dryer
operates in a manner that is typical of
tunnel dryers, which are exempt from
NSPS subpart UUU.
Abstract for [0600018]
Q: Does 40 CFR part 60, subpart SS,
apply to surface coating operations at
the Nestaway facility in McKenzie,
Tennessee, which fabricates and coats
wire racks that are sold for use in new
dishwashers of various manufacturers
and as aftermarket replacements?
A: No. EPA finds that because the
facility is not part of a large appliance
PO 00000
Frm 00031
Fmt 4703
Sfmt 4703
assembly plant, NSPS subpart SS does
not apply to its surface coating
operation.
Abstract for [0600019]
Q: What requirements under 40 CFR
part 60, subpart KKKK, would apply to
a simple cycle combustion turbine to be
operated at the Stock Island Power Plant
in Key West, Florida, since the Florida
Municipal Power Agency and GE
Packaged Power entered into a contract
for the fabrication and construction of
the turbine on February 18, 2005, the
final date by which a unit must have
commenced construction to be treated
as an existing unit not subject to NSPS
subpart KKKK?
A: EPA finds that additional
documentation must be submitted to
make a determination. Without
adequate documentation that the
February 18, 2005 contract for the
fabrication and construction of the
turbine will result in a continuous
program of construction, the
combustion turbine in question would
be considered subject to NSPS subpart
KKKK requirements for new affected
facilities. Refer to ADI determination
0600021.
Abstract for [0600020]
Q: Does EPA approve an exemption
from opacity monitoring under 40 CFR
part 60, subpart UUU, for a flash dryer
that uses baghouses to control emissions
as it dries product at the DuPont DeLisle
titanium dioxide production facility in
Pass Christian, Mississippi?
A: Yes. EPA finds that because the
dryer has a particulate matter emission
rate of less than 11 tons/year, an
exemption from the opacity monitoring
requirement of NSPS subpart UUU is
appropriate.
Abstract for [0600021]
Q: What requirements under 40 CFR
part 60, subpart KKKK, would apply to
a simple cycle combustion turbine to be
operated at the Stock Island Power Plant
in Key West, Florida, since the Florida
Municipal Power Agency and GE
Packaged Power entered into a contract
for the fabrication and construction of
the turbine on February 18, 2005, the
final date by which a unit must have
commenced construction to be treated
as an existing unit not subject to NSPS
subpart KKKK. The facility has
provided follow-up information in
response to EPA’s request for more
information. Refer to ADI determination
0600019.
A: Based on the information
submitted, EPA concludes that the
combustion turbine, construction of
which commenced on February 18,
E:\FR\FM\04DEN1.SGM
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Federal Register / Vol. 71, No. 232 / Monday, December 4, 2006 / Notices
2005, will not be subject to NSPS
subpart KKKK, provided that a
continuous program of construction is
maintained and construction is
completed within a reasonable time.
Abstract for [0600022]
Q: Does EPA allow the owners or
operators of certain affected facilities
under 40 CFR part 60, subpart Dc to
submit reports annually instead of each
six-month period, as required by 40 CFR
60.48(c)(j), if a facility is not required to
obtain a Title V permit?
A: No. EPA finds that the reporting
frequency in NSPS subpart Dc is
intended to apply to owners and
operators of affected facilities regardless
of whether they are required to obtain
a Title V permit.
Abstract for [0600023]
Q: Does 40 CFR part 60, subpart OOO,
apply to air classifiers at nonmetallic
mineral processing plants?
A: EPA finds that air classifiers are
regulated by NSPS subpart OOO if they
are part of a grinding mill. A grinding
mill is the only affected facility under
NSPS subpart OOO that includes air
classifiers. If air classifiers are not part
of a grinding mill, then they are not
regulated by the standard since these are
not identified as a separate category in
the rule.
mstockstill on PROD1PC61 with NOTICES
Abstract for [0600024]
Q: Does EPA find that 40 CFR part 60,
subpart UUU, applies to the Line 2 ore
dryer and product dryer at the DuPont
DeLisle Plant in Pass Christian,
Mississippi, where the facility uses a
chlorination-oxidation process to
manufacture titanium dioxide pigment?
A: Yes. EPA finds that although the
chlorination-oxidation process is
exempt from NSPS subpart UUU, the
ore dryer and product dryer at the
DuPont plant are not part of the
chlorination-oxidation process. Thus,
the dryers are subject to NSPS subpart
UUU.
Abstract for [0600025]
Q: Does EPA find that the
requirements of the 25 Pennsylvania
(PA) Code Chapter 139 and the PA
Department of Environmental Protection
(PADEP) Continuous Source Monitoring
Manual can be applied in lieu of the
requirements in 40 CFR part 60,
subparts A and D, and 40 CFR part
60.13, for sulfur dioxide (SO2) emissions
for two power boilers at Weyerhaeuser’s
Johnsonburg Mill in Johnsonburg,
Pennsylvania?
A: Yes. EPA finds that the
requirements of 25 PA Code Chapter
139 and PADEP’s Continuous Source
VerDate Aug<31>2005
11:51 Dec 01, 2006
Jkt 211001
Monitoring Manual can be applied in
lieu of corresponding NSPS
requirements in CFR part 60, subparts A
and D and 40 CFR part 60.13, provided
that SO2 emissions from the two power
boilers remain less than 0.20 lbs/mmBtu
and provided that, for validating hourly
averages, the source computes one hour
averages from 6 or more data points
equally spaced over the one-hour
period.
Abstract for [0600026]
Q: Does EPA approve EPA Method 9
visible emissions observations as an
alternative to installing and certifying a
continuous opacity monitoring system
(COMS) when oil is burned in a boiler
subject to 40 CFR part 60, subpart Dc,
at the Penreco plant in Karns City,
Pennsylvania?
A: Yes. EPA finds that the alternative
opacity monitoring can be performed in
lieu of installing and certifying a COMS.
However, specific procedures outlined
in EPA’s response must be followed to
ensure compliance with this approval
under NSPS subpart Dc. The procedures
are consistent with those that EPA has
approved for other Subpart Dc boilers
that burn gas as a primary fuel and that
have an annual capacity factor of 10
percent or less for oil when used as a
backup fuel.
Abstract for [0600027]
Q: Do the changes at the glass melting
furnace, Furnace 52, cause an emissions
increase at the Flat River Glass facility
in Park Hills, Missouri, and if so, was
the increase accomplished through a
capital expenditure such that it would
be considered a modification pursuant
to 40 CFR part 60, subparts A and CC?
Refer to ADI Control No. 0600028.
A: Yes. EPA finds that the changes at
the furnace constitute a capital
expenditure and therefore, the furnace
has been modified for purposes of NSPS
subparts A and CC. This determination
provides further detail on the
equipment considered in the
calculations, the estimated cost of the
changes, and the results of the
calculation that show a capital
expenditure.
Abstract for [0600028]
Q1: Do the physical or operational
changes to Furnace 52 at the Flat River
Glass facility in Park Hills, Missouri,
result in an emissions increase pursuant
to 40 CFR part 60, subparts A and C?
Refer to ADI determination 0600027.
A1: Yes. Based on evaluation of the
AP–42 factors, historical test data, and
40 CFR part 60, Appendix C
calculations, EPA has determined that
Furnace 52 has been modified since a
PO 00000
Frm 00032
Fmt 4703
Sfmt 4703
70391
kilogram per hour emission increase did
occur as a result of the change, and that
such modification was accomplished
with a capital expenditure.
Q2: Was the emissions increase
accomplished through a capital
expenditure pursuant to 40 CFR 60.14(e)
at the Flat River Glass facility in Park
Hills, Missouri?
A2: Yes. EPA finds that there was a
capital expenditure made for purposes
of NSPS subpart CC. Based on the
information submitted, EPA has
determined that the cost of the changes
made to the furnace exceeded 12
percent of the facility’s basis, the
threshold for a capital expenditure.
Because the company did not include
any cost data for the initial installation
of the glass furnace, the existing
facility’s basis was calculated by using
the current cost of a new glass furnace
and back-calculating the cost to the year
of installation.
Abstract for [0600029]
Q: Does EPA find that a source’s
intent in incurring costs of component
replacement as a result of SIP control
requirements should be a factor in
determining whether a source has
exceeded the 50 percent cost threshold
of the NSPS reconstruction provisions
under 40 CFR part 60, subpart A?
A: EPA finds that replacement costs
may not be disregarded based on the
owner’s intent in incurring them.
Creating an intent-based exemption for
owners whose SIP-related expenditures
pass the 50 percent threshold in Section
60.15 would be inconsistent with
Section 111. However, EPA could
conclude in the future that only certain
facilities should be considered new
once the 50 percent threshold for
reconstruction is surpassed.
Alternatively, EPA could determine that
it is appropriate to exempt sources in
individual cases or to exempt
identifiable groups of sources where
NSPS compliance is not
‘‘technologically or economically
feasible,’’ which is consistent with
section 111 of the Clean Air Act.
Abstract for [Z060003] and [M060035]
Q: Does EPA find that benzene
emissions that occur from heat
exchanger leaks at a facility, located in
Texas and represented by Baker Botts,
are to be included in the calculation of
the Total Annual Benzene (TAB)
quantity from facility waste water under
the NESHAP for Benzene Waste
Operations, 40 CFR part 61, subpart FF?
A: Yes. EPA finds that neither
benzene emissions occurring from noncontact heat exchanger leaks into
cooling tower water nor benzene
E:\FR\FM\04DEN1.SGM
04DEN1
70392
Federal Register / Vol. 71, No. 232 / Monday, December 4, 2006 / Notices
quantities from ‘‘contact heat
exchangers’’ qualify for the exemption
or exclusion from the required benzene
calculation (TAB) under the NESHAP
for Benzene Waste Operations, 40 CFR
part 61, subpart FF. Therefore, waste in
the form of gases or vapors that is
emitted from process fluids is required
to be part of the calculation of the total
annual benzene quantity in facility
waste generation. This determination is
based on the fact that the benzene
emissions are directly generated by the
respective process, and are neither the
result of leakage nor of process offgas.
Abstract for [0600082]
Q: Does EPA approve a request for an
alternative monitoring plan for a
hydrogen production facility to allow
grab sampling of refinery fuel gas
combusted in the two reformer furnaces
on a staggered schedule, as opposed to
installing a continuous emissions
monitoring system (CEMS), under 40
CFR part 60, subpart J, at the Air
Products and Chemicals hydrogen
production facility at the Exxon Mobil
refinery in Joliet, Illinois?
A: Yes. EPA conditionally approves
the request for an alternative monitoring
plan under NSPS subpart J, provided
the facility meets the conditions and
terms of approval specified in EPA’s
response. This AMP approval is
consistent with the EPA guidance
entitled ‘‘Alternative Monitoring Plan
for NSPS Subpart J Refinery Fuel Gas:
Conditions for Approval of the
Alternative Monitoring Plan for
Miscellaneous Refinery Fuel Gas
Streams.’’
Dated: November 22, 2006.
Lisa C. Lund,
Acting Director, Office of Compliance.
[FR Doc. E6–20440 Filed 12–1–06; 8:45 am]
BILLING CODE 6560–50–P
FEDERAL RESERVE SYSTEM
Proposed Agency Information
Collection Activities; Comment
Request
Board of Governors of the
Federal Reserve System
SUMMARY: Background
On June 15, 1984, the Office of
Management and Budget (OMB)
delegated to the Board of Governors of
the Federal Reserve System (Board) its
approval authority under the Paperwork
Reduction Act, as per 5 CFR 1320.16, to
approve of and assign OMB control
numbers to collection of information
requests and requirements conducted or
sponsored by the Board under
mstockstill on PROD1PC61 with NOTICES
AGENCY:
VerDate Aug<31>2005
11:51 Dec 01, 2006
Jkt 211001
conditions set forth in 5 CFR 1320
Appendix A.1. Board–approved
collections of information are
incorporated into the official OMB
inventory of currently approved
collections of information. Copies of the
Paperwork Reduction Act Submission,
supporting statements and approved
collection of information instruments
are placed into OMB’s public docket
files. The Federal Reserve may not
conduct or sponsor, and the respondent
is not required to respond to, an
information collection that has been
extended, revised, or implemented on or
after October 1, 1995, unless it displays
a currently valid OMB control number.
Request for comment on information
collection proposal
The following information collection,
which is being handled under this
delegated authority, has received initial
Board approval and is hereby published
for comment. At the end of the comment
period, the proposed information
collection, along with an analysis of
comments and recommendations
received, will be submitted to the Board
for final approval under OMB delegated
authority. Comments are invited on the
following:
a. Whether the proposed collection of
information is necessary for the proper
performance of the Federal Reserve’s
functions; including whether the
information has practical utility;
b. The accuracy of the Federal
Reserve’s estimate of the burden of the
proposed information collection,
including the validity of the
methodology and assumptions used;
c. Ways to enhance the quality,
utility, and clarity of the information to
be collected; and
d. Ways to minimize the burden of
information collection on respondents,
including through the use of automated
collection techniques or other forms of
information technology.
DATES: Comments must be submitted on
or before February 2, 2007.
ADDRESSES: You may submit comments,
identified by FR 4004 (OMB No. 7100–
0112), by any of the following methods:
• Agency Web Site: https://
www.federalreserve.gov. Follow the
instructions for submitting comments at
https://www.federalreserve.gov/
generalinfo/foia/ProposedRegs.cfm.
• Federal eRulemaking Portal: https://
www.regulations.gov. Follow the
instructions for submitting comments.
• E–mail:
regs.comments@federalreserve.gov.
Include the OMB control number in the
subject line of the message.
• FAX: 202–452–3819 or 202–452–
3102.
PO 00000
Frm 00033
Fmt 4703
Sfmt 4703
• Mail: Jennifer J. Johnson, Secretary,
Board of Governors of the Federal
Reserve System, 20th Street and
Constitution Avenue, N.W.,
Washington, DC 20551.
All public comments are available
from the Board’s web site at
www.federalreserve.gov/generalinfo/
foia/ProposedRegs.cfm as submitted,
unless modified for technical reasons.
Accordingly, your comments will not be
edited to remove any identifying or
contact information. Public comments
may also be viewed electronically or in
paper in Room MP–500 of the Board’s
Martin Building (20th and C Streets,
NW.) between 9 a.m. and 5:00 p.m. on
weekdays.
FOR FURTHER INFORMATION CONTACT: A
copy of the proposed form and
instructions, the Paperwork Reduction
Act Submission, supporting statement,
and other documents that will be placed
into OMB’s public docket files once
approved may be requested from the
agency clearance officer, whose name
appears below.
Michelle Long, Federal Reserve Board
Clearance Officer (202–452–3829),
Division of Research and Statistics,
Board of Governors of the Federal
Reserve System, Washington, DC 20551.
Telecommunications Device for the Deaf
(TDD) users may contact (202–263–
4869), Board of Governors of the Federal
Reserve System, Washington, DC 20551.
Proposal to approve under OMB
delegated authority the extension for
three years, without revision, of the
following report:
Report title: Written Security Program
for State Member Banks
Agency form number: FR 4004
OMB control number: 7100–0112
Frequency: On occasion
Reporters: State member banks
Annual reporting hours: 35 hours
Estimated average hours per response:
0.5 hours
Number of respondents: 70
General description of report: This
recordkeeping requirement is
mandatory pursuant to section 3 of the
Bank Protection Act [12 U.S.C. §
1882(a)] and Regulation H [12 CFR §
208.61]. Because written security
programs are maintained at state
member banks, no issue of
confidentiality under the Freedom of
Information Act normally arises.
However, copies of such documents
included in examination work papers
would, in such form, be confidential
pursuant to exemption 8 of the Freedom
of Information Act [5 U.S.C. § 552(b)(8)].
Abstract: Each state member bank
must develop and implement a written
security program and maintain it in the
E:\FR\FM\04DEN1.SGM
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Agencies
[Federal Register Volume 71, Number 232 (Monday, December 4, 2006)]
[Notices]
[Pages 70383-70392]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E6-20440]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
[FRL-8250-5]
Recent Posting to the Applicability Determination Index (ADI)
Database System of Agency Applicability Determinations, Alternative
Monitoring Decisions, and Regulatory Interpretations Pertaining to
Standards of Performance for New Stationary Sources, National Emission
Standards for Hazardous Air Pollutants, and the Stratospheric Ozone
Protection Program
AGENCY: Environmental Protection Agency (EPA).
ACTION: Notice of availability.
-----------------------------------------------------------------------
SUMMARY: This notice announces applicability determinations,
alternative monitoring decisions, and regulatory interpretations that
EPA has made under the New Source Performance Standards (NSPS); the
National Emission Standards for Hazardous Air Pollutants (NESHAP); and
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 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 CFR part 60 and 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 broadly termed applicability
determinations. See 40 CFR 60.5 and 61.06. Although the 40 CFR part 63
NESHAP and section 111(d) of the Clean Air Act (CAA) regulations
contain no specific regulatory provision that sources may request
applicability determinations, EPA does respond to written inquiries
regarding applicability for the 40 CFR part 63 and section 111(d) of
the CAA programs. The NSPS and NESHAP also allow sources to seek
permission to use monitoring or recordkeeping which is different from
the promulgated requirements. See 40 CFR 60.13(i), 61.14(g),
63.8(b)(1), 63.8(f), and 63.10(f). EPA's written responses to these
inquiries are broadly termed 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 broadly
termed regulatory interpretations.
EPA currently compiles EPA-issued NSPS and NESHAP applicability
determinations, alternative monitoring decisions, and regulatory
interpretations, and posts them on the Applicability Determination
Index (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 and NESHAP. 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 63 such documents added to
the ADI on November 10, 2006. The subject, author, recipient, date 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.
The following table identifies the database control number for each
document posted on the ADI database system on November 10, 2006; 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.
----------------------------------------------------------------------------------------------------------------
Control Category Subpart Title
----------------------------------------------------------------------------------------------------------------
0600001.................... NSPS....................... Dc........................ Alternative Fuel
Monitoring.
0600002.................... NSPS....................... BB........................ Exemption from TRS
Standard for Brown Stock
Washer.
0600003.................... NSPS....................... BB........................ Alternative Monitoring for
Scrubber.
0600004.................... NSPS....................... Db, Dc.................... Fuel Supplier
Certification Statements.
0600006.................... NSPS....................... J......................... Alternative Monitoring
Plan for a Catalytic
Cracking Unit.
0600007.................... NSPS....................... J......................... Alternative Monitoring
Plan for a Flare.
0600008.................... NSPS....................... AAa....................... Alterations to an Electric
Arc Furnace.
0600082.................... NSPS....................... A, J...................... Alternative Monitoring
Plan for Hydrogen
Production Facility.
M060001.................... MACT....................... MMM....................... Compliance Test Waiver
Request.
M060002.................... MACT....................... MMMM...................... Post Vulcanized Rubber-to-
Metal Parts Bonding.
[[Page 70384]]
M060003.................... MACT....................... DDDDD..................... Common Duct Testing and
Acid Rain Program Opt-in.
M060004.................... MACT....................... DDDDD..................... Firetube Boilers.
M060005.................... MACT....................... EEE....................... Liquid-to-Gas Ratio
Operating Parameter
Limit.
M060006.................... MACT....................... IIII...................... Use of Previously
Conducted Transfer
Efficiency Test.
M060007.................... MACT....................... MM........................ Alternative Monitoring for
Scrubber.
M060008.................... MACT....................... A, EEE.................... Alternative Monitoring
Locations and Parameters.
M060009.................... MACT....................... A, EEE.................... Alternative Monitoring
Plan for Hazardous Waste
Combustor.
Z060001.................... NESHAP..................... FF, V..................... Alternative Monitoring
Plan for Dual Purpose
Valves.
0600009.................... NSPS....................... WWW....................... Landfill Gas Processing
System as Treatment.
0600010.................... NSPS....................... WWW....................... Landfill Gas Processing
System as Treatment.
0600011.................... NSPS....................... WWW....................... Landfill Gas Processing
System as Treatment.
0600012.................... NSPS....................... WWW....................... Landfill Gas Processing
System as Treatment.
0600013.................... NSPS....................... WWW....................... Landfill Gas Processing
System as Treatment.
0600014.................... NSPS....................... WWW....................... Temperature Monitors in
Gas Turbines.
0600015.................... NSPS....................... VV........................ Liquid Urea Manufacturing
Operations.
A060001.................... Asbestos................... M......................... Demolition under Control
of Same Owner or
Operator.
A060002.................... Asbestos................... M......................... Removal of Floor Mastic
Using a Mechanical
Buffer.
A060003.................... Asbestos................... M......................... Applicability of 260
Linear Feet Requirement.
A060004.................... Asbestos................... M......................... Test Method for Spray-
applied Acoustical
Materials.
A060005.................... Asbestos................... M......................... Regulated Asbestos
Containing Material.
A060006.................... Asbestos................... M......................... Meaning of Preclude Access
and Dripping.
M060010.................... MACT....................... HH, HHH................... Clarification of Ownership
and Co-location.
M060011.................... MACT....................... NNN....................... Metal Building Insulation.
M060012.................... MACT....................... MMMM...................... Post Vulcanized Rubber-to-
Metal Parts Bonding.
M060013.................... MACT....................... PPP....................... Use of Tetrahydrofuran
(THF) as Raw Material.
M060014.................... MACT....................... H......................... Nitrile Stripper Column
System.
M060015.................... MACT....................... FFFF, HHHHH............... Non-Dedicated Mixing
Vessels.
0600016.................... NSPS....................... A, G...................... Modification of Nitric
Acid Plant.
0600017.................... NSPS....................... UUU....................... Tile Dryers.
0600018.................... NSPS....................... SS........................ Coating of Dishwasher
Racks.
0600019.................... NSPS....................... A, KKKK................... Commencement of
Construction.
0600020.................... NSPS....................... UUU....................... Opacity Monitoring
Exemption.
0600021.................... NSPS....................... A, KKKK................... Commencement of
Construction.
0600022.................... NSPS....................... Dc........................ Reporting Frequency
Requirements.
0600023.................... NSPS....................... OOO....................... Air Classifiers.
0600024.................... NSPS....................... UUU....................... Titanium Dioxide Ore
Dryers and Product
Dryers.
0600025.................... NSPS....................... A, D...................... State Monitoring
Requirements in Lieu of
40 CFR Part 60.
0600026.................... NSPS....................... Dc........................ Alternative Opacity
Monitoring.
0600027.................... NSPS....................... A, CC..................... Modification and Capital
Expenditure Calculations.
0600028.................... NSPS....................... A, CC..................... Modification and Capital
Expenditure Calculations.
0600029.................... NSPS....................... A......................... SIP-mandated Expenditures
and Reconstruction.
M060016.................... MACT....................... G......................... Once In/Always In Rule.
M060017.................... MACT....................... YY........................ Dry Spinning Spandex
Production Process Units.
M060018.................... MACT....................... HHHHH, MMMM............... Coating of Test Panels Not
Used in Final Product.
M060019.................... MACT....................... MM........................ Alternative Monitoring of
Smelt Dissolving Tank
Scrubber.
M060020.................... MACT....................... JJJJ, OOOO................ Point of Determination for
Group of Coating Lines.
M060021.................... MACT....................... NNNNN..................... Alternative Monitoring
Plan for HCL Scrubber.
M060022.................... MACT....................... S......................... Alternative Monitoring
Parameters for a Dual
Control System.
M060023.................... MACT....................... S......................... Clean Condensate
Alternative & Creditable
Reductions.
M060024.................... MACT....................... S......................... Applicability of White
Liquor Oxidation System.
M060025.................... MACT....................... EEEEE..................... Molding and Core Making.
M060026.................... MACT....................... S......................... Clean Condensate
Alternative & Creditable
Reductions.
Z060003.................... NESH....................... FF........................ Benzene Emissions from
Exchange Leaks.
----------------------------------------------------------------------------------------------------------------
Summary of Headers and Abstracts
Abstracts
Abstract for [A060001]
Q: Are residential structures that are demolished as part of a
larger project, such as highway expansion, subject to the asbestos
requirements under 40 CFR part 61, subpart M?
A: Yes. EPA finds, pursuant to 40 CFR 61.145, that if two or more
residences under the control of the same owner or operator are part of
a larger demolition project, such as highway expansion, they are
subject to the asbestos regulation, NESHAP subpart M.
Abstract for [A060002]
Q1: Is floor mastic a Category 1 asbestos-containing material under
40 CFR part 61, subpart M?
A1: No. EPA finds that floor mastic is not a Category 1 asbestos-
containing material under the Asbestos NESHAP. However, pursuant to 40
CFR 61.141, it is a Category II asbestos-containing material.
Q2: Does the use of a mechanical buffer with an abrasive pad on
floor mastic cause the floor mastic to become friable, and thus a
Regulated Asbestos-Containing Material (RACM) under 40 CFR part 61,
subpart M?
A2: Yes. EPA finds that pursuant to 40 CFR 61.141, the use of a
mechanical buffer with an abrasive pad causes floor mastic to become
friable and, thus, it is considered a RACM under the asbestos NESHAP.
Abstract for [A060003]
Q: Does the regulatory threshold of 260 linear feet on pipes apply
to caulking and roof flashing materials that qualify as regulated
asbestos-containing material (RACM) under 40 CFR part 61, subpart M?
A: No. EPA finds the 260 linear feet threshold is applicable only
to pipes
[[Page 70385]]
under the asbestos NESHAP. Other materials, such as caulking or roof
flashing, are subject to the 160 square foot standard as specified in
40 CFR 61.145.
Abstract for [A060004]
Q1: Has EPA issued guidance specifically about spray-applied
acoustical materials under 40 CFR part 61, subpart M?
A1: No. EPA has not issued guidance under the asbestos NESHAP
specifically about spray-applied acoustical materials.
Q2: Does EPA recommend that the public assure spray-applied
acoustical materials to contain asbestos without testing, and, what
method(s) should be used to test these materials under 40 CFR part 61,
subpart M?
A2: No. EPA is not recommending that the public assure spray-
applied acoustical materials to contain asbestos without testing. In
regards to testing spray-applied acoustical materials, Polarized Light
Microscopy (PLM) is specified in 40 CFR part 63 as the approved testing
method; however, Transmission Electron Microscopy (TLM) is also an
acceptable method.
Abstract for [A060005]
Q: Does 40 CFR part 61, subpart M, require that all asbestos-
containing materials be removed before the demolition of a facility?
A: No. The asbestos NESHAP does not require all asbestos-containing
materials to be removed before demolition. However, all Regulated
Asbestos Containing Material (RACM) must be removed from a facility
being demolished or renovated before any activity begins that would
break up, dislodge, or similarly disturb the material or preclude
access to the material for subsequent removal.
Abstract for [A060006]
Q: Could EPA clarify the meaning of the words ``preclude access''
and ``dropping'' in 40 CFR 61.145(c)(1) and 61.145(c)(6) of the
asbestos NESHAP, subpart M?
A: EPA finds that the use of the term ``preclude access'' in 40 CFR
61.145(c)(1) of the asbestos NESHAP is intended to ensure that all
Regulated Asbestos Containing Material (RACM) expected to be disturbed
during the demolition or renovation is removed from the facility before
any action is taken that could prevent safe removal of the RACM during
a later phase of the project. The use of the term ``dropping'' is
intended to prevent RACM from falling (instead of being ``placed'') on
the floor and to ensure that RACM is moved in a careful way to minimize
asbestos fiber release.
Abstract for [M060001]
Q: Does EPA waive the Method 5 test requirement for a second
process vent, under 40 CFR part 63, subpart MMM, at the Arkema facility
in Riverview, Michigan?
A: Yes. EPA waives the Method 5 test because information submitted
by the facility shows that it is impractical to test the second vent
due to short operating time, low flow rate, and low pressure drop. Dust
emissions will be drawn through the first vent which will be tested,
and any remaining dust will be trapped in the vent collection tank or
in the mineral oil scrubbers.
Abstract for [M060002]
Q: Does EPA find that a coating being applied at the Cooper Tire &
Rubber facility in Findlay, Ohio, that uses the same methodology,
composition, and function as a rubber-to-metal coating, but that is
bonded during a heating process not involving the vulcanization of
rubber, is a rubber-to-metal coating under 40 CFR part 63, subpart
MMMM?
A: No. EPA finds that because the bonding process is not performed
during the vulcanization process, it is not considered a rubber-to-
metal coating and should not be included in that category. Instead, the
coating is subject to the general use coating subcategory emission
limit in 40 CFR 63.3890(b)(1).
Abstract for [M060003]
Q1: Can the required emission tests, under 40 CFR part 63, subpart
DDDDD, be conducted in the common duct for boilers 1, 2, and 3 at the
Dairyland Power Cooperative Alma Station in LaCrosse, Wisconsin?
A1: No. 40 CFR 63.7510 requires that each unit be tested, and the
language in Section II.F of the September 13, 2004 Preamble to the
Final Rule reinforces this requirement. The facility is required to
submit an alternative test procedure request with appropriate technical
justification, if it wants to conduct common duct testing. However,
testing in a common duct is considered a minor change to a test method;
thus, EPA Regions and delegated States may approve such a request.
Q2: Does EPA find that boilers 1, 2, and 3 would be exempt from the
boiler MACT, under 40 CFR part 63, subpart DDDDD, if they opt into the
Acid Rain Program?
A2: No. EPA finds that 40 CFR 63.7491 includes no such exemption. A
source cannot avoid controlling mercury emissions by agreeing to
control sulfur dioxide and nitrogen oxides.
Abstract for [M060004]
Q: Does EPA find that the two 250-horsepower firetube boilers
planned for installation at Green Bay Packaging in Green Bay,
Wisconsin, should be regulated within the ``small gaseous fuel
subcategory'' as defined in MACT subpart DDDDD, 40 CFR 63.7575, even if
each boiler's heat input rating at 100 percent efficiency may reach
10.5 million BTU per hour?
A: Yes. EPA finds that these boilers are regulated within the
``small gaseous fuel subcategory'' as that term is defined in MACT
subpart DDDDD, 40 CFR 63.7575. In response to comments, the Agency
agreed to add firetube boilers to the definition of small liquid fuel
and gaseous fuel subcategories in the final rule.
Abstract for [M060005]
Q: Does EPA approve a request from Minnesota Mining & Manufacturing
Company (3M), under 40 CFR part 63, subpart EEE, to establish a high
energy wet scrubber's hydrogen chloride/chlorine liquid-to-gas ratio
operating parameter limit for a hazardous waste incinerator unit that
is equal to 20.4 gallons per 1,000 dry standard cubic feet based upon
the data from 3M's September 1 and 2, 2004, comprehensive performance
test and not upon the data from 3M's July 2001, Resource Conservation
and Recovery Act Trial Burn?
A: No. EPA does not approve the request because the company has not
demonstrated that the proposed hydrogen chloride/chlorine liquid-to-gas
ratio operating parameter limit also corresponds to compliance with the
particulate matter, semi-volatile metal, and low volatile metals
emission standards.
Abstract for [M060006]
Q: Does EPA approve at the General Motors (GM) Orion Assembly Plant
in Orion, Michigan, the use of the results of a transfer efficiency
test conducted in December 2004 for the primer surfacer and topcoat
operations in lieu of performing another transfer efficiency test,
under 40 CFR part 63, subpart IIII?
A: Yes. EPA approves the use of the December 2004 test results for
the primer surfacer and the topcoat operations in lieu of performing an
initial test to determine transfer efficiency. The test meets the
requirements of MACT subpart IIII, 40 CFR 63.3160(c). There have been
no process or equipment changes since the test that would trigger
retesting, and the required operating parameters and transfer
efficiency were established during the test.
[[Page 70386]]
Abstract for [M060007]
Q: Does EPA approve the continuous monitoring of fan amps and total
scrubbing liquid flow rate as an alternative to the scrubber monitoring
parameters required by NSPS Subpart BB and NESHAP Subpart MM, at the
Weyerhaeuser Company facility in Bennettsville, South Carolina?
A: Yes. EPA approves this alternative continuous monitoring plan
under MACT subpart MM and NSPS subpart BB because the dynamic scrubber
operates near atmospheric pressure and the proposed monitoring is an
acceptable alternative. Consistent with the requirements of 40 CFR
63.864, fan amps and scrubber liquid flow rate must be monitored at
least once each successive 15-minute period, and continuous compliance
must be determined based on a 3-hour average.
Abstract for [M060008]
Q1: Does EPA approve the request for an alternative monitoring
location to continuously monitor total hydrocarbons and carbon
monoxide, under 40 CFR part 63, subpart EEE, at the Ash Grove Cement
Company facility in Overland Park, Kansas?
A1: Yes. EPA approves the request to monitor hydrocarbons in the
by-pass and between stages numbers 2 and 3 of the preheater instead of
in the main stack, pursuant to MACT subpart EEE, 40 CFR 63.1209(g)(1)
and 63.8(f). Both the bypass and preheater gas streams must have a
hydrocarbon limit of 10 ppmv on an hourly rolling average basis as
defined in MACT subpart EEE. The location of the hydrocarbon monitors
must be as specified in the Comprehensive Performance Test Plan,
downstream of the bypass baghouse, while the preheater monitor shall be
located in the gas stream between stages numbers 2 and 3 of the pre-
heater in a manner that ensures a representative sample of gas will be
monitored.
Q2: Does EPA also approve the request for an alternative method to
calculate the maximum gas temperature at the inlet to the facility's
particulate matter control device, under 40 CFR part 63, subpart EEE?
A2: Yes. EPA approves this request for an alternative calculation
pursuant to MACT subpart EEE, 40 CFR 63.1209(g)(1) and 63.8(f) due to
the potential danger associated with operating the coal mill baghouse
at an elevated temperature. The facility will establish that the
maximum gas temperature at the inlet of the coal mill baghouse does not
exceed 200 degrees Fahrenheit. Establishing the maximum gas temperature
at the inlet is an alternative for the coal mill baghouse only.
Q3: Does EPA also approve the request for an alternative to
calculate the minimum combustion chamber temperature limit as required
by 40 CFR 63.1209(j)(1) and (k)(2)?
A3: No. EPA does not approve the request to set the minimum
combustion chamber temperature as the average of the highest hourly
rolling averages measured in each trial run burn. However, EPA finds
the source could establish a minimum combustion chamber temperature by
matching the combustion chamber temperature profile during the
comprehensive performance test using the specific procedures described
in EPA's response as an alternative to establishing the minimum
combustion chamber temperature.
Abstract for [M060009]
Q: Does EPA approve the alternative monitoring request to
continuously monitor oxygen and temperature instead of carbon monoxide
or total hydrocarbons, under 40 CFR part 63, subpart EEE, at the Holcim
facility in Clarksville, Montana?
A: Yes. EPA approves this alternative monitoring request pursuant
to MACT subpart EEE, 40 CFR 63.1209(g)(1) and 63.8(f), provided the
facility meets the conditions established for the performance test for
destruction and removal efficiency (DRE) that demonstrates compliance
with the DRE standard found in 40 CFR 63.1204(c), and carbon monoxide
and total hydrocarbon standards found in 40 CFR 63.1204(a)(5), as
indicated in EPA's response.
Abstract for [M060010]
Q: Could EPA clarify the relationship between ownership and co-
location in regards to the applicability of 40 CFR part 63, subpart HH,
to the Mocane Cryogenic/Compressor Station located near Forgan,
Oklahoma, and owned by Regency Gas Services and Colorado Interstate
Gas?
A: EPA finds that all the facility operations are located at a
single site, as defined in 40 CFR 63.761 of MACT subpart HH, and,
because the transmission and storage source category begins where
natural gas enters the transmission pipeline, the site is subject to
MACT subpart HH. EPA also finds the equipment qualifies as a single
Title V source with all equipment subject to Title V permitting.
Because of separate ownership, individual Title V permits will be
issued to the owner of the specific equipment.
Abstract for [M060011]
Q: Does 40 CFR part 63, subpart NNN, apply to the metal building
insulation produced at CertainTeed's facility in Kansas City, Kansas?
A: Yes. EPA finds that metal building insulation meets the
definition of building insulation for purposes of MACT subpart NNN, and
that production of this insulation at the CertainTeed facility is
subject to MACT subpart NNN.
Abstract for [M060012]
Q: Does EPA find that an autoclave should be included in the
rubber-to-metal or general use subcategory, under 40 CFR part 63,
subpart MMMM, if a partial vulcanization occurs in the first heating
step and the part is submitted fully vulcanized in the autoclave, as is
the case of the Cooper Standard Automotive facility in Michigan?
A: EPA finds that the autoclave should be included in the rubber-
to-metal subcategory under MACT subpart MMMM. EPA has determined that
the second coating step of a metal insert bonded to rubber does involve
vulcanization based on the stress test results done on two metal parts
coated with the same adhesive, and should be included in such
subcategory.
Abstract for [M060013]
Q: Does EPA find that the substantive control, testing, and
monitoring requirements of 40 CFR part 63, subpart PPP, apply to the 3M
process using tetrahydrofuran (THF) as a raw material at the Specialty
Material Manufacturing facility in Cottage Grove, Minnesota?
A: Yes. EPA finds that the language at 40 CFR 63.1420(d)(3) only
exempts those processes which produce polyether polyols from epoxide
polymerization, and, by its terms, does not extend the exemption under
MACT subpart PPP to processes which produce polyether polyols from THF.
The facility did not provide the Agency sufficient information to
determine whether only the recordkeeping or demonstration requirements
at 40 CFR 63.1420(b)(1) would apply to the process.
Abstract for [M060014]
Q1: Does EPA find that the nitrile stripper column (NSC) system at
the INVISTA S.a.r.l. (INVISTA) Victoria plant should be classified as a
waste management unit or a recovery device, under 40 CFR part 63,
subpart PPP, or can it be subject to two sets of requirements at the
same time because it may qualify both as a waste management and a
recovery device under the Hazardous Organic National Emissions Standard
for Hazardous Air
[[Page 70387]]
Pollutants (HON) rule, 40 CFR part 63, subpart F?
A1: EPA finds that the NSC system cannot be subject to two sets of
standards under the HON rule and that it should be classified as a
waste management unit under that rule. Based on the concept of
``discarded'' within the terms ``point of determination'' and
``wastewater'' in the HON rule, the NSC system must either be a
recovery device within the CMPU or a waste management unit outside of
the CMPU. The fact that the NSC system is receiving the stormwater
stream from the Victoria plant, in addition to the stream from the ADN
unit for which it was originally designed, clarifies for the Agency
that the NSC system is outside of the CMPU. The liquid stream
transferred from the ADN process to the NSC system is, therefore,
``discharged'' to the NSC system. This makes the NSC system a ``waste
management unit'' and the ADN stream ``wastewater'', subject to the
performance standards of 40 CFR 63.138 of the HON rule.
Q2: What is the appropriate classification for the NSC system if
the stormwater runoff is no longer routed to the ADN unit?
A2: When the stormwater runoff is removed from the NSC system, the
NSC system should be evaluated as a recovery device because the NSC
system potentially serves the purpose of recovering chemicals for fuel
value, use, reuse or for sale for fuel value, use or reuse.
Abstract for [M060015]
Q: Could EPA clarify the applicability of the Miscellaneous Organic
Chemical Manufacturing NESHAP (MON rule) and the Miscellaneous Coating
Manufacturing NESHAP (MCM rule), under 40 CFR part 63, subparts FFFF
and HHHHH respectively, to non-dedicated mixing vessels which support
coatings manufacturing in three different areas at the Cytec Industries
facility in Havre de Grace, Maryland?
A: EPA determines that in area one the non-dedicated HAP mixing
vessels are used in the production of ``pre-react'' isolated
intermediates which are stored below ambient temperature until further
processing to produce a coating occurs, and therefore, are subject to
the MON. The pre-react is similar to a synthesis operation producing a
MON chemical described by SIC code 289, rather than a coating. EPA
agrees that since the ``pre-react'' meets all of the criteria specified
in EPA's response, it is a MON product and therefore the mixing vessel
that produces it is subject to the MON. In area two, the MON chemical
is mixed with curing systems, fillers, and other additives, and a
coating is produced. Since the non dedicated HAP mixing vessels in area
two are associated with the production of a coating, they are part of
the miscellaneous coating manufacturing subject to the MCM rule. Area
three consists of the application of the coating produced in area two.
Neither the MON nor the MCM apply to the application of coatings.
Abstract for [M060016]
Q: Does MACT subpart G, pursuant to 40 CFR 63.100(b)(4), provide
minor source status to International Specialty Products' butanediol
facility in Lima, Ohio, given that the facility is no longer part of
the BP Amoco Chemical Company (BP) major source; has actual emissions
of less than 2 tpy of individual hazardous air pollutants (HAP) and
less than 4 tpy of total HAP; shares no common control or ownership
with BP; and is a discrete facility that is not contiguous with any BP
property or any of the remaining sources listed on the current BP Title
V permit?
A: No. EPA finds that the facility is not eligible for minor source
status under MACT subpart G. It was constructed and permitted as a
major source on the compliance date for new sources in the HON. Thus,
according to the ``once in, always in'' policy, it remains subject to
the HON rule, even if it subsequently reduces its emissions below major
source thresholds.
Abstract for [M060017]
Q: Does 40 CFR part 63, subpart YY, apply to the spandex production
equipment at the Invista facility in Waynesboro, Virginia, where the
equipment is part of one or more dry spinning spandex production
process units?
A: No. EPA finds that the spandex production equipment is not
subject to MACT subpart YY. 40 CFR 63.1103(h)(1)(ii) defines emission
points, listed in paragraphs (h)(1)(i)(A) through (C), that are
associated with a dry spinning spandex production process unit that are
not subject to the requirements of 40 CFR 63.1103(h)(3) even though the
process is part of the spandex production source category.
Abstract for [M060018]
Q: Does 40 CFR part 63, subpart MMMM, apply to a spray booth at the
PPG Industries, Inc. (PPG) facility in Springdale, Pennsylvania, that
would be used to prepare painted sample panels to be tested at a
laboratory?
A: No. EPA determines that PPG's proposed new spray booth would not
be subject to NESHAP subpart MMMM, the Surface Coating of Miscellaneous
Metal Parts and Products rule, since the spray booth would not be used
to apply surface coating of ``miscellaneous metal parts or products,''
which include certain various ``industrial, household, and consumer
products,'' or their ``metal components,'' i.e., parts, as defined in
40 CFR 63.3881. The sample panels that PPG plans to prepare in its new
spray booth do not qualify as ``industrial, household, and consumer
products'' because they will be prepared solely to allow coatings to be
tested in a laboratory, will not be sold in commerce, and will
eventually be recycled as scrap metal. The sample panels also do not
qualify as ``metal components'' of ``industrial, household, and
consumer products'' because the panels will never become part of an
industrial, household, or consumer product.
Abstract for [M060019]
Q: Does EPA approve continuous monitoring of fan amperage and
scrubbing liquid flow rate in lieu of scrubber pressure drop under 40
CFR part 63, subpart MM, for the smelt dissolving tank scrubber at the
Smurfit-Stone Container Hopewell Mill in Hopewell, Virginia?
A: Yes. EPA finds that pressure drop is not the best indicator of
control device performance for low-energy entrainment scrubbers.
Compliance with MACT subpart MM could be demonstrated by verifying ID
fan operation, maintaining a scrubber liquid flow rate, and maintaining
a scrubbing liquid supply pressure based on established parameters from
the facility's performance test.
Abstract for [M060020]
Q: Does EPA agree that the Point of Determination (POD) for the
predominant use ratio (e.g., 90 percent/10 percent) which, according to
40 CFR 63.4281(e), would determine whether part 63, subpart OOOO
(``Fabric NESHAP'') or subpart JJJJ (``Paper and Other Web Coating
NESHAP, POWC NESHAP'') would apply, can be located at the entry point
to the common control device for the Cytec Engineered Materials Inc.
facility in Havre de Grace, Maryland?
A: No. EPA does not approve Cytec's request to consider the entry
point to the common control device for the four coaters/dryers as a POD
for purposes of establishing the MACT subpart OOOO predominant use
ratio. 40 CFR 63.4281(e) states that ``any web coating line must comply
with the subpart of this part that applies to the predominant use
activity conducted at the affected
[[Page 70388]]
source.'' This indicates that a predominant use determination under the
Fabric NESHAP can be made only with respect to a single coating line,
not groups of coating lines. Therefore, Cytec, Inc. must assure ensure
that its three coaters/dryers subject to POWC NESHAP comply with all of
the POWC NESHAP's requirements, and that its one coater/dryer subject
to the Fabric NESHAP complies with all of the Fabric NESHAP's
requirements.
Abstract for [M060021]
Q: Does EPA approve, under 40 CFR part 63, subpart NNNNN, the
monitoring of alternative operating limit parameters (scrubber base
temperature and indicators of proper liquid flow) at the DuPont
Washington Works facility in Washington, West Virginia?
A: Yes. EPA finds that DuPont has demonstrated that the scrubber
monitoring specified under MACT subpart NNNNN is not appropriate for
its process, and that the proposed alternative monitoring meets the
requirements for approval in 40 CFR 63.9025(b) and 63.8(f).
Abstract for [M060022]
Q: Does EPA approve monitoring the secondary power from the
electrostatic precipitator (ESP) as an alternative monitoring parameter
to monitoring pressure drop on the scrubber, under 40 CFR part 63,
subpart S, for a dual-control device consisting of an ESP followed by a
packed tower scrubber at the International Paper Georgetown Mill, in
Georgetown, South Carolina?
A: No. EPA does not approve monitoring secondary power from the ESP
in-lieu-of monitoring the pressure drop on the scrubber because there
is no demonstration to show that the negative electric charge on
particles exiting the ESP will have anything more than negligible
effects on the efficiency of the scrubber.
Abstract for [M060023]
Q: Does EPA approve that emission reductions achieved as a result
of upgrades to a wastewater lagoon at the Buckeye facility in Perry,
Florida, are creditable to demonstrate compliance with the condensate
collection requirements in 40 CFR 63.446(c) of the Pulp and Paper MACT,
40 CFR part 63, subpart S?
A: EPA determines that the reductions may be creditable provided
that Buckeye can provide the necessary data to satisfactorily
demonstrate continuous compliance with the lb/ODTP compliance option
for condensate collection and treatment, beginning at the initial
compliance date, as described in EPA's response. The data would be
generally considered creditable if it demonstrates that such emission
reductions resulted from efficiency improvements to a control device
that can be verified; are clearly from additional improvements in
technology; and are not otherwise needed to meet regulatory
requirements.
Abstract for [M060024]
Q: Does EPA find that the White Liquor Oxidation (WLOx)
system portion of a pulp and paper mill's oxygen delignification system
subject to the requirements of the Pulp and Paper MACT, 40 CFR part 63,
subpart S, at the Palatka Mill in Palatka, Florida?
A: No. EPA finds that the WLOx system is not named as
one of the pieces of process equipment in the regulatory definition of
an oxygen delignification system and therefore is not subject to the
MACT subpart S requirements in 40 CFR 63.443.
Abstract for [M060025]
Q: Does EPA find that mold and core making lines that use the
``Expandable Pattern Casting'' (or ``Lost Foam'') process at the
Mueller Company's facility in Albertville, Alabama subject to the MACT
requirements for Iron and Steel Foundries under 40 CFR part 63, subpart
EEEEE?
A: Yes. The pouring, cooling, and shakeout operations of Mueller's
Expendable Pattern Casting process are not significantly different than
a conventional sand casting operation, and therefore should be
considered as such for 40 CFR part 63, subpart EEEEE purposes. In
addition, Mueller's pouring operations would be classified as pouring
stations, not pouring areas. The main distinctions between a pouring
station and a pouring area are that pouring stations are automated and
that the pouring can reasonably be assumed to occur at distinct points.
Abstract for [M060026]
Q: Does EPA approve that emission reductions resulting from
improvements to the pulp washer line fans, under 40 CFR part 63,
subpart S, creditable for the Pulp & Paper MACT Clean Condensate
Alternative (CCA) at the Smurfit-Stone facility in Fernandina Beach,
Florida?
A: No. Generally, a mill can make efficiency improvements to a
control device and then use the incremental improvements for CCA credit
if the emission changes are verifiable and clearly from additional
improvements in technology. The modifications described for this
facility are not additional improvements in technology, but rather
equipment upgrades to meet proper operating levels and result in HAP
reductions from emissions that should never have been emitted.
Abstract for [Z060001]
Q: Does EPA approve an alternative monitoring plan for pressure/
vacuum relief valves, under 40 CFR part 61, subpart FF, for the
wastewater treatment plant tanks and oil-water separator at the Flint
Hills Resources refinery in Saint Paul, Minnesota?
A: Yes. EPA concludes that the pressure/vacuum relief valves
function as both pressure relief devices and dilution air openings.
Further, the Agency recognizes that the requirements of 40 CFR
61.343(a)(1)(i)(B) and (C) do not account for this dichotomy, and it
approves the proposed alternative monitoring plan under NESHAP subpart
FF to resolve the conflicting requirements.
Abstract for [0600001]
Q: Does EPA approve an alternative monitoring plan altering the
required daily monitoring, under 40 CFR part 60, subpart Dc, 40 CFR
60.48c(g), to a monthly monitoring schedule for natural gas fuel usage
at the Ypsilanti Community Utilities Authority facility in Ypsilanti,
Michigan?
A: Yes. EPA conditionally approves the alternative monitoring
request to record natural gas usage for two new boilers on a monthly,
rather than a daily basis. EPA finds that compliance with NSPS Subpart
Dc can be adequately verified by keeping fuel usage records on a
monthly basis if only natural gas is burned. The facility must also
specify how the total fuel usage will be apportioned to individual
boilers.
Abstract for [0600002]
Q: Does EPA approve an exemption from the Total Reduced Sulfur
(TRS) standard in NSPS subpart BB, 40 CFR 60.283(a)(1)(iv), for the
brown stock washer (BSW) system at the Buckeye Florida Limited
Partnership facility in Perry, Florida?
A: Yes. Based on cost information supplied and recent cost
estimates from other facilities, EPA finds that the BSW system
qualifies for a temporary exemption under NSPS subpart BB. Should
future changes make the control of TRS emissions from the Number 2 Mill
BSW system cost effective, this exemption will no longer apply, and it
will be necessary for Buckeye to control TRS emissions.
Abstract for [0600003]
Q: Does EPA approve the continuous monitoring of fan amps and the
total
[[Page 70389]]
scrubbing liquid flow rate as an alternative to the scrubber monitoring
parameters required by 40 CFR part 60, subpart BB, and 40 CFR part 63,
subpart MM, for a smelt dissolving tank dynamic scrubber at the
Weyerhaeuser Company facility in Bennettsville, South Carolina?
A: Yes. EPA approves these alternative monitoring parameters. The
dynamic scrubber operates near atmospheric pressure and thus the
proposed monitoring, in combination with monitoring of scrubber liquid
flow rate, is an acceptable alternative to the NESHAP subpart MM
requirement to monitor the pressure loss of the gas stream and the
scrubbing liquid flow rate. In addition, EPA approves the request to
monitor scrubbing liquid flow rate as an alternative to the NSPS
subpart BB requirement to monitor scrubber liquid supply pressure.
Abstract for [0600004]
Q: Does EPA exempt facilities which use very low sulfur oil from
the requirement to obtain certifications of sulfur content for each
shipment of fuel oil delivered, under 40 CFR part 60, subparts Db and
Dc, and permit them to provide only receipts indicating the type of
fuel delivered?
A: No. EPA does not exempt facilities from the requirement to
obtain certifications of sulfur content for shipments of fuel oil. The
requirements of NSPS subparts Db and Dc regarding certification of fuel
sulfur content must be met.
Abstract for [0600006]
Q: Does EPA approve a request for an exemption from the requirement
in NSPS subpart J, 40 CFR 60.105(a)(2)(ii), to install, calibrate,
operate, and maintain a carbon monoxide continuous emission monitor
with a 1,000-ppmv span gas for a fluid catalytic cracking unit at the
Flint Hills Resources facility in Saint Paul, Minnesota?
A: Yes. EPA finds that the facility qualifies for the exemption set
forth in 40 CFR 60.105(a)(2)(ii) because the company has met the
following requirements: calibrated a CO CEM with a span value of 100
parts per million by volume, dry basis (PPMVD); demonstrated that the
relative accuracy is 10 percent of the average CO emissions or 5 PPM
CO, whichever is greater; and demonstrated that the average CO
emissions during a 30-day period are less than 50 PPMVD with the CO
CEM. The facility still must comply with a state air permit requirement
to install and maintain a CO CEM with a 100 PPMV span.
Abstract for [0600007]
Q: Does EPA approve an alternative monitoring plan for a zinc
thermal oxidizer flare used during periods of maintenance or
malfunction of a vapor recovery unit at a gasoline loading rack, under
40 CFR part 60, subpart J, at the Flint Hills Resources facility in
Saint Paul, Minnesota?
A: Yes. EPA finds that the company has demonstrated that this
refinery fuel gas meets the criteria in EPA's guidance for refinery
fuel gas stream alternative monitoring plans and approves the
alternative monitoring plan.
Abstract for [0600008]
Q1: Does EPA find that the alterations made in 1985 to electric arc
furnace (EAF) number 2 at Oregon Steel Mill's facility in Portland,
Oregon, meet the definition of ``modification'' under 40 CFR part 60,
subpart AAa?
A1: No. Based on the information provided, EPA finds that the
alterations made in 1985 to EAF number 2 do not constitute a
modification under NSPS subpart AAa. Although the alterations increased
the production rate of steel from 25 tons per hour to 50 tons per hour,
they did not increase particulate matter emissions.
Q2: Does EPA find that the alterations meet the definition of
``reconstruction'' under 40 CFR part 60, subpart AAa?
A2: No. Based on the information provided, EPA finds that the
changes made in 1985 to EAF number 2 do not constitute a reconstruction
under NSPS subpart AAa. Reconstruction is based on a comparison of the
fixed capital cost of the new components and a comparable entirely new
facility, that is, a new eccentric bottom tap EAF capable of producing
50 tons of steel per hour. The EAF consists of the furnace shell and
roof and the transformer. The cost of the 1985 alterations was 31.8
percent of the cost of the comparable entirely new facility, which is
less than the 50 percent reconstruction cost threshold.
Q3: Does EPA find that the other changes made to the EAF number
that resulted in an increase on the potential emission rate was
accomplished with a ``capital expenditure'' as defined under 40 CFR
part 60, subpart AAa?
A3: No. EPA finds that the changes made in 1987, 1990, 1991, 1993,
1997 and 1998 to EAF number 2 did not require capital expenditures as
defined in 40 CFR 60.2. The annual asset guideline repair allowance
percentage for an EAF is 18 percent. The changes that enabled increases
in production rate included the purchase of a transformer and the
installation of oxy-fuel burners, a post combustion system, aluminum
current arms, and other changes, all of which did not cost more than 18
percent of the basis for an EAF.
Abstract for [0600009]
Q: Does EPA find that the gas processing system at the Bethel
Landfill in Hampton, Virginia, qualifies as treatment under NSPS
subpart WWW, pursuant to 40 CFR 60.752(b)(2)(iii)(C)?
A: Yes. EPA considers compression, filtration, and moisture removal
from a landfill gas for use in eight reciprocating internal combustion
engines to be treatment pursuant to 40 CFR 60.752(b)(2)(iii)(C).
Because the engines will be exempt from monitoring, they do not have to
be included in the Startup, Shutdown, and Malfunction Plan (SSM Plan)
required by 40 CFR part 63, subpart AAAA. However, the treatment system
supplying gas to the turbines will have to be included in the SSM Plan.
Abstract for [0600010]
Q: Does EPA consider the gas processing system that includes the
three turbines at the Grand Central Landfill in Pen Argyl,
Pennsylvania, to be treatment under 40 CFR part 60, subpart WWW,
pursuant to 40 CFR 60.752(b)(2)(iii)(C)?
A: Yes. EPA considers compression, filtration, and moisture removal
from a landfill gas for use in an energy recovery device to be
treatment under NSPS subpart WWW, pursuant to 40 CFR
60.752(b)(2)(iii)(C). Because the engines will be exempt from
monitoring, they do not have to be included in the Startup, Shutdown,
and Malfunction Plan (SSM Plan) required by 40 CFR part 63, subpart
AAAA. However, the treatment system supplying gas to the turbines will
have to be included in the SSM Plan. Also, Pennsylvania may include
state enforceable requirements in any permit it issues, based on its
review of state laws and regulations.
Abstract for [0600011]
Q: Does EPA consider the gas processing system at Keystone Potato
Products' facility in Hegins, Pennsylvania, to be treatment under 40
CFR part 60, subpart WWW?
A: Yes. EPA considers compression, filtration, and moisture removal
from a landfill gas for use in an energy recovery device to be
treatment under NSPS subpart WWW, pursuant to 40 CFR
60.752(b)(2)(iii)(C). Because the engines will be exempt from
monitoring, they do not have to be included in the Startup, Shutdown,
and Malfunction Plan (SSM Plan) required by 40 CFR Part 63, subpart
AAAA. However, the treatment system supplying gas to the turbines
[[Page 70390]]
will have to be included in the SSM Plan. Also, Pennsylvania may
include state enforceable requirements in any permit it issues, based
on its review of state laws and regulations.
Abstract for [0600012]
Q: Does EPA consider the gas processing system at the Lake View
Landfill in Philadelphia, Pennsylvania, to be treatment under 40 CFR
part 60, subpart WWW?
A: Yes. EPA considers compression, filtration, and moisture removal
from a landfill gas for use in an energy recovery device to be
treatment under NSPS subpart WWW, pursuant to 40 CFR
60.752(b)(2)(iii)(C). Because the engines will be exempt from
monitoring, they do not have to be included in the Startup, Shutdown,
and Malfunction Plan (SSM Plan) required by 40 CFR Part 63, subpart
AAAA. However, the treatment system supplying gas to the turbines will
have to be included in the SSM Plan.
Abstract for [0600013]
Q: Does EPA consider gas processing system to be treatment as
specified under 40 CFR part 60, subpart WWW at the Modern Landfill
facility in York, Pennsylvania?
A: Yes. EPA considers compression, filtration, and moisture removal
from a landfill gas for use in an energy recovery device to be
treatment under NSPS subpart WWW, pursuant to 40 CFR
60.752(b)(2)(iii)(C). Because the engines will be exempt from
monitoring, they do not have to be included in the Startup, Shutdown,
and Malfunction Plan (SSM Plan) required by 40 CFR Part 63, subpart
AAAA. However, the treatment system supplying gas to the turbines will
have to be included in the SSM Plan.
Abstract for [0600014]
Q: Does EPA approve the use of post-combustion chamber temperature
monitors as an alternative to combustion chamber temperature monitors
in turbines at the Pottstown Landfill facility in Pottstown,
Pennsylvania, required by 40 CFR part 60, subpart WWW?
A: Yes. EPA has determined that the location of the temperature
monitors on these turbines is acceptable as an alternative to being
located in the combustion zone of the turbines.
Abstract for [0600015]
Q: Does 40 CFR part 60, subpart VV, apply to liquid urea
manufacturing operations?
A: EPA has not provided a site-specific determination in this case
because the source has not been identified. Additionally, EPA is not
prepared to issue a blanket exemption for liquid urea manufacturing
operations as none was issued during the rulemaking process. In
addition, a liquid urea facility must look to the same criteria in 40
CFR 60.480(a) and (b) as other manufacturers of listed chemicals to
determine whether it is subject to NSPS subpart VV. The facility must
then consider whether it might be exempted under 40 CFR 60.480(d).
Abstract for [0600016]
Q: Will plant changes to increase production capacity result in a
modification of the C-1 Nitric Acid Plant located at the PCS Nitrogen
Fertilizer facility in Augusta, Georgia? Is the use of pre-change and
post-change emission testing the appropriate means of determining
whether the change results in an increase in the NOX
emission rate that will trigger the finding of a modification?
A: Yes. EPA finds that the plant changes do constitute a
modification under the NSPS, and the unit would become subject to NSPS
subpart G. EPA also finds that the manner in which the Masar emission
control system has been operated in the past and its improper
maintenance makes it impossible to establish rational pre-change test
conditions for purposes of determining whether the plant changes will
cause an increase in NOX emission rate. In this case,
emission factors are the most appropriate method to determine if an
emission increase occurs, and the appropriate factors show that the
increase in nitric acid production capacity will result in an emission
increase. Thus, the plan will be subject to NSPS subpart G requirements
following the proposed production rate increase.
Abstract for [0600017]
Q: Does 40 CFR part 60, subpart UUU, apply to a tile dryer at the
Florim USA facility in Clarksville, Tennessee, that dries formed tiles
by convection?
A: No. EPA finds that the tile dryer operates in a manner that is
typical of tunnel dryers, which are exempt from NSPS subpart UUU.
Abstract for [0600018]
Q: Does 40 CFR part 60, subpart SS, apply to surface coating
operations at the Nestaway facility in McKenzie, Tennessee, which
fabricates and coats wire racks that are sold for use in new
dishwashers of various manufacturers and as aftermarket replacements?
A: No. EPA finds that because the facility is not part of a large
appliance assembly plant, NSPS subpart SS does not apply to its surface
coating operation.
Abstract for [0600019]
Q: What requirements under 40 CFR part 60, subpart KKKK, would
apply to a simple cycle combustion turbine to be operated at the Stock
Island Power Plant in Key West, Florida, since the Florida Municipal
Power Agency and GE Packaged Power entered into a contract for the
fabrication and construction of the turbine on February 18, 2005, the
final date by which a unit must have commenced construction to be
treated as an existing unit not subject to NSPS subpart KKKK?
A: EPA finds that additional documentation must be submitted to
make a determination. Without adequate documentation that the February
18, 2005 contract for the fabrication and construction of the turbine
will result in a continuous program of construction, the combustion
turbine in question would be considered subject to NSPS subpart KKKK
requirements for new affected facilities. Refer to ADI determination
0600021.
Abstract for [0600020]
Q: Does EPA approve an exemption from opacity monitoring under 40
CFR part 60, subpart UUU, for a flash dryer that uses baghouses to
control emissions as it dries product at the DuPont DeLisle titanium
dioxide production facility in Pass Christian, Mississippi?
A: Yes. EPA finds that because the dryer has a particulate matter
emission rate of less than 11 tons/year, an exemption from the opacity
monitoring requirement of NSPS subpart UUU is appropriate.
Abstract for [0600021]
Q: What requirements under 40 CFR part 60, subpart KKKK, would
apply to a simple cycle combustion turbine to be operated at the Stock
Island Power Plant in Key West, Florida, since the Florida Municipal
Power Agency and GE Packaged Power entered into a contract for the
fabrication and construction of the turbine on February 18, 2005, the
final date by which a unit must have commenced construction to be
treated as an existing unit not subject to NSPS subpart KKKK. The
facility has provided follow-up information in response to EPA's
request for more information. Refer to ADI determination 0600019.
A: Based on the information submitted, EPA concludes that the
combustion turbine, construction of which commenced on February 18,
[[Page 70391]]
2005, will not be subject to NSPS subpart KKKK, provided that a
continuous program of construction is maintained and construction is
completed within a reasonable time.
Abstract for [0600022]
Q: Does EPA allow the owners or operators of certain affected
facilities under 40 CFR part 60, subpart Dc to submit reports annually
instead of each six-month period, as required by 40 CFR 60.48(c)(j), if
a facility is not required to obtain a Title V permit?
A: No. EPA finds that the reporting frequency in NSPS subpart Dc is
intended to apply to owners and operators of affected facilities
regardless of whether they are required to obtain a Title V permit.
Abstract for [0600023]
Q: Does 40 CFR part 60, subpart OOO, apply to air classifiers at
nonmetallic mineral processing plants?
A: EPA finds that air classifiers are regulated by NSPS subpa