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, 80392-80407 [E8-31117]
Download as PDF
80392
Federal Register / Vol. 73, No. 251 / Wednesday, December 31, 2008 / Notices
Under section 6(f)(1)(A) of FIFRA,
registrants may request, at any time, that
their pesticide registrations be canceled
or amended to terminate one or more
pesticide uses. Section 6(f)(1)(B) of
FIFRA requires that before acting on a
request for voluntary cancellation, EPA
must provide a 30–day public comment
period on the request for voluntary
cancellation or use termination. In
addition, section 6(f)(1)(C) of FIFRA
requires that EPA provide a 180–day
comment period on a request for
voluntary cancellation or termination of
any minor agricultural use before
granting the request, unless:
1. The registrant requests a waiver of
the comment period, or
2. The Administrator determines that
continued use of the pesticide would
pose an unreasonable adverse effect on
the environment.
The fomesafen registrant has
requested that EPA waive the 180–day
comment period. EPA will provide a
30–day comment period on the
proposed request.
Unless a request is withdrawn by the
registrant within 30 days of publication
of this notice, or if the Agency
determines that there are substantive
comments that warrant further review of
this request, an order will be issued
canceling the affected registrations.
TABLE 1.— FOMESAFEN PRODUCT
REGISTRATIONS WITH PENDING REQUESTS FOR CANCELLATION
Registration
Number
Product
Name
Company
7969-82
BAS 530
04 H
herbicide.
BASF
7969-83
FASTER
TM herbicide.
BASF
Table 2 of this unit includes the name
and address of record for the registrant
of the products listed in Table 1 of this
unit.
TABLE 2.— REGISTRANT REQUESTING
VOLUNTARY CANCELLATION
EPA Company
Number
pwalker on PROD1PC71 with NOTICES
7969
Company Name and
Address
17:41 Dec 30, 2008
Jkt 217001
V. Procedures for Withdrawal of
Request and Considerations for
Reregistration of Fomesafen
Registrants who choose to withdraw a
request for cancellation must submit
such withdrawal in writing to the
person listed under FOR FURTHER
INFORMATION CONTACT, postmarked
before January 30, 2009. This written
withdrawal of the request for
cancellation will apply only to the
applicable FIFRA section 6(f)(1) request
listed in this notice. If the products(s)
have been subject to a previous
cancellation action, the effective date of
cancellation and all other provisions of
any earlier cancellation action are
controlling.
VI. Provisions for Disposition of
Existing Stocks
Existing stocks are those stocks of
registered pesticide products which are
currently in the United States and
which were packaged, labeled, and
released for shipment prior to the
effective date of the cancellation action.
In any order issued in response to this
request for cancellation of product
registrations, EPA proposes to include
the following provisions for the
treatment of any existing stocks of the
products identified or referenced in
Table 1 in Unit III. Registrants may sell
and distribute existing stocks for 1 year
from the date of the use termination
request. The products may be sold,
distributed, and used by people other
than the registrant until existing stocks
have been exhausted, provided that
such sale, distribution, and use
complies with the EPA-approved label
and labeling of the product.
If the request for voluntary
cancellation is granted, the Agency
intends to publish the cancellation
order in the Federal Register.
List of Subjects
BASF, 26 Davis Drive,
Triangle Park, North
Carolina 27709-3528
IV. What is the Agency’s Authority for
Taking this Action?
Section 6(f)(1) of FIFRA provides that
a registrant of a pesticide product may
VerDate Aug<31>2005
at any time request that any of its
pesticide registrations be canceled or
amended to terminate one or more uses.
FIFRA further provides that, before
acting on the request, EPA must publish
a notice of receipt of any such request
in the Federal Register. Thereafter,
following the public comment period,
the Administrator may approve such a
request.
Environmental protection, Pesticides
and pests.
Steven Bradbury,
Director, Special Review and Reregistration
Division, Office of Pesticide Programs.
[FR Doc. E8–31009 Filed 12–30–08; 8:45 am]
BILLING CODE 6560–50–S
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ENVIRONMENTAL PROTECTION
AGENCY
[FRL–8759–4]
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 control
number, date, author, subpart, or subject
search. For questions about the ADI or
this notice, contact Maria Malave at EPA
by phone at: (202) 564–7027, or by
e-mail at: malave.maria@epa.gov. For
technical questions about the individual
applicability determinations or
monitoring decisions, refer to the
contact person identified in the
individual documents, or in the absence
of a contact person, refer to the author
of the document.
SUPPLEMENTARY INFORMATION:
Background: The General Provisions to
the NSPS in 40 Code of Federal
Regulations (CFR) part 60 and the
NESHAP in 40 CFR part 61 provide that
a source owner or operator may request
a determination of whether certain
intended actions constitute the
commencement of construction,
reconstruction, or modification. EPA’s
written responses to these inquiries are
commonly referred to as applicability
determinations. See 40 CFR 60.5 and
61.06. Although the part 63 NESHAP
and section 111(d) of the Clean Air Act
regulations contain no specific
E:\FR\FM\31DEN1.SGM
31DEN1
Federal Register / Vol. 73, No. 251 / Wednesday, December 31, 2008 / Notices
regulatory provision that sources may
request applicability determinations,
EPA does respond to written inquiries
regarding applicability for the part 63
and section 111(d) programs. The NSPS
and NESHAP also allow sources to seek
permission to use monitoring or
recordkeeping that are different from the
promulgated requirements. See 40 CFR
60.13(i), 61.14(g), 63.8(b)(1), 63.8(f), and
63.10(f). EPA’s written responses to
these inquiries are commonly referred to
as alternative monitoring decisions.
Furthermore, EPA responds to written
inquiries about the broad range of NSPS
and NESHAP regulatory requirements as
they pertain to a whole source category.
These inquiries may pertain, for
example, to the type of sources to which
the regulation applies, or to the testing,
monitoring, recordkeeping or reporting
requirements contained in the
regulation. EPA’s written responses to
these inquiries are commonly referred to
as regulatory interpretations.
EPA currently compiles EPA-issued
NSPS and NESHAP applicability
determinations, alternative monitoring
decisions, and regulatory
interpretations, and posts them on the
ADI on a quarterly basis. In addition,
the ADI contains EPA-issued responses
to requests pursuant to the stratospheric
ozone regulations, contained in 40 CFR
part 82. The ADI is an electronic index
on the Internet with over one thousand
EPA letters and memoranda pertaining
to the applicability, monitoring,
recordkeeping, and reporting
requirements of the NSPS 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 107 such documents added to the
ADI on December 12, 2008 and
December 23, 2008. 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.
80393
Summary of Headers and Abstracts
The following table identifies the
database control number for each
document posted on the ADI database
system on December 12, 2008 and
December 23, 2008; the applicable
category; the subpart(s) of 40 CFR part
60, 61, or 63 (as applicable) covered by
the document; and the title of the
document, which provides a brief
description of the subject matter.
We have also included an abstract of
each document identified with its
control number after the table. These
abstracts are provided solely to alert the
public to possible items of interest and
are not intended as substitutes for the
full text of the documents. This notice
does not change the status of any
document with respect to whether it is
‘‘of nationwide scope or effect’’ for
purposes of section 307(b)(1) of the
Clean Air Act. For example, this notice
does not make an applicability
determination for a particular source
into a nationwide rule. Neither does it
purport to make any document that was
previously non-binding into a binding
document.
ADI DETERMINATIONS UPLOADED ON DECEMBER 12, 2008
Control number
Category
Subpart
Title
Alternative Monitoring Plan for Refinery Fuel Gas.
Force Majeure Events Delaying Initial Performance Testing for an Iron and Steel Foundry.
Disapproval of Alternative Stack Testing Request.
Request to Substitute Flue Gas Temperature Monitoring for Pressure Drop Monitoring.
Control Requirement for Plant Exhaust from Primary Bag Filter Vents when Routed and not Routed
to a Cogeneration Unit.
Continuous Compliance Requirements for Mercury Recovery Units.
Storage and Transfer of Toluene Used as Fuel.
Multiple Standard Batches to Define a Process within a Single MCPU.
MON Rule and Pharmaceuticals NESHAP for Glucosamine Hydrochloride.
A080001
M080005
M080006
M080007
M080008
...........
...........
...........
...........
...........
NSPS ........
MACT .......
MACT .......
MACT .......
MACT .......
J ...........
EEEEE
EEEEE
DDDDD
YY ........
M080009
M080010
M080011
M080012
...........
...........
...........
...........
MACT
MACT
MACT
MACT
IIIII ........
EEEEE
FFFF ....
GGG,
FFFF.
FFFF ....
MMM,
SS.
GGG .....
MMM,
SS.
N ..........
RRR .....
UUUU ...
F ...........
Db ........
WWW ...
WWW ...
WWW ...
J, Ja .....
WWW ...
WWW ...
WWW ...
CC ........
WWW ...
Db, Dc ..
UUU .....
D ..........
D ..........
KKKK ...
VV, VVa
J ...........
.......
.......
.......
.......
MACT .......
MACT .......
M080016 ...........
M080017 ...........
pwalker on PROD1PC71 with NOTICES
M080013 ...........
M080014 ...........
MACT .......
MACT .......
M080018 ...........
M080019 ...........
M080020 ...........
Z080003 ............
800017 ..............
800018 ..............
800019 ..............
800020 ..............
800021 ..............
800022 ..............
800023 ..............
800024 ..............
800025 ..............
800026 ..............
800027 ..............
800028 ..............
800029 ..............
800030 ..............
800031 ..............
800032 ..............
800033 ..............
MACT .......
MACT .......
MACT .......
NESHAP ...
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
VerDate Aug<31>2005
17:41 Dec 30, 2008
Jkt 217001
Manufacture of Poly Methyl Methacrylate (PMMA) Acrylic Sheet.
Initial Compliance Demonstration for Thermal Treatment Units.
Process Condensers and 20 ppmv Limit without Calculating Uncontrolled Emissions.
Use of Previously Conducted Performance Tests for Initial Compliance Demonstration.
Alternative Testing, Monitoring, and Work Practice Standards.
Request for Waiver of Performance Tests for Low-speed Aluminum Scrap Shredders.
Request for Alternative Monitoring Plan Following Replacement of GC/PID Instrument.
Alternative Monitoring Plan Modification.
Alternative Monitoring Procedure for Opacity.
Alternative Monitoring Requests.
Alternative Monitoring Requests.
Alternative Monitoring Requests.
Gap in Continuous Program of Construction for Process Heater.
Request for Higher Operating Temperature at Landfill Wellhead.
Request for Higher Operating Temperature at Landfill Wellhead.
Alternative Compliance Timeline for Landfill.
Bridgewall Optical Temperature (BWOT) Alternative Monitoring Proposal.
Alternative Compliance Timeline for Landfill Well.
Indirect-Fired Dryers used in the Ethanol Industry.
Synthetic Alumina Applicability Determination.
Continuous Particulate Emission Monitoring System.
Continuous Particulate Emission Monitoring System.
Reconstruction of a Stationary Combustion Turbine.
Alternative Monitoring Procedure for Leak Detection.
Revised Alternative Monitoring Plan Conditions for Hydrogen Sulfide.
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80394
Federal Register / Vol. 73, No. 251 / Wednesday, December 31, 2008 / Notices
ADI DETERMINATIONS UPLOADED ON DECEMBER 12, 2008—Continued
Control number
800034
800035
800036
800037
800038
800039
800040
800041
800042
800043
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
Category
NSPS
NSPS
NSPS
NSPS
NSPS
NSPS
NSPS
NSPS
NSPS
NSPS
........
........
........
........
........
........
........
........
........
........
pwalker on PROD1PC71 with NOTICES
800044 ..............
800045 ..............
M080021 ...........
M080022 ...........
M080023 ...........
M080024 ...........
M080025 ...........
M080026 ...........
M080027 ...........
M080028 ...........
M080029 ...........
M080031 ...........
M080034 ...........
M080035 ...........
Z080004 ............
800046 ..............
800047 ..............
800048 ..............
800049 ..............
800050 ..............
800051 ..............
800052 ..............
800053 ..............
800054 ..............
800055 ..............
800056 ..............
800057 ..............
800058 ..............
800059 ..............
800060 ..............
800061 ..............
800062 ..............
800063 ..............
800064 ..............
800065 ..............
800066 ..............
800067 ..............
800068 ..............
800069 ..............
800070 ..............
800071 ..............
800072 ..............
800073 ..............
800074 ..............
800075 ..............
800076 ..............
800077 ..............
800078 ..............
800079 ..............
NSPS ........
NSPS ........
MACT .......
MACT .......
MACT .......
MACT .......
MACT .......
MACT .......
MACT .......
MACT .......
MACT .......
MACT .......
MACT .......
MACT .......
NESHAP ...
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NESHAP ...
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
800080 ..............
800081 ..............
800082 ..............
800083 ..............
800084 ..............
800085 ..............
800086 ..............
800087 ..............
M080037 ...........
M080036 ...........
0800088 ............
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
NSPS ........
MACT .......
MACT .......
NSPS ........
VerDate Aug<31>2005
17:41 Dec 30, 2008
Subpart
Dc .........
WWW ...
KKK ......
UUU .....
WWW ...
WWW ...
WWW ...
Kb .........
Kb .........
GG,
KKKK.
Da ........
Da ........
RRR .....
NNNNN
RRR .....
KKKK ...
G ..........
G ..........
RRR .....
RRR .....
CC, R ...
DDDDD
FFFFF ..
JJJJ ......
E ...........
DD ........
WWW ...
J ...........
J ...........
J ...........
E ...........
UUU .....
WWW ...
WWW ...
J ...........
OOO .....
WWW ...
WWW ...
WWW ...
WWW ...
WWW ...
WWW ...
WWW ...
WWW ...
WWW ...
WWW ...
WWW ...
WWW ...
WWW ...
WWW ...
GG .......
WWW ...
BB ........
OOO .....
AAa ......
J ...........
WWW ...
WWW ...
AAAA,
WWW.
J ...........
J ...........
J ...........
DD ........
OOO .....
WWW ...
WWW ...
H ..........
RRR .....
RRR .....
J ...........
Jkt 217001
Title
Boiler Derate Proposal.
Alternative Compliance Timeline for Landfill Well.
Applicability to Expansion Project at Propane Refrigeration Plant.
Alternative Monitoring for Calciner.
Alternative Compliance Timeline for Leachate Recirculation Line.
Alternative Timeline to Correct Positive Pressure at Landfill Wells.
Alternative Standards/Procedures for Oxygen/Pressure.
Process Tanks Defined.
Request for Reconsideration of Gasoline Storage Vessel Decision.
Original owner/operator of Gas Turbine.
Modification to Increase Feed Rate with Bottleneck.
Modification to Increase Feed Rate with Bottleneck.
Applicability to Aluminum Shredder/Baler.
Alternative Monitoring for Water Scrubber/Mist Eliminator.
Thermal Chip Dryer Operation Prior to Performance Testing.
Applicability determination for Metal Can Surface Coating NESHAP.
Alternative Monitoring Parameters for HON Carbon Adsorber System.
Alternative Monitoring Parameters for HON Carbon Adsorber System.
Dioxin/Furan Stack Test Waiver Request.
Dioxin/Furan State Test Waiver Request, OM & M Plan Deficiencies, and Lime Injection.
Alternate Monitoring Parameter for Assist Gas in Flare.
Definition of Process Heater.
Stack Test Waiver Request.
Compliance Demonstration for Paper and Other Web Coating.
Applicability for Sludge Dryer.
Applicability and Alternative Control Conditions for Malting Facility.
Treated Landfill Gas Exemption.
Alternative Monitoring Plan at Petroleum Refinery.
Alternative Monitoring for Petroleum Refinery Vapor Combustion Unit.
Alternative Monitoring for Petroleum Refinery Vapor Combustion Unit.
Waiver of Mercury Emissions Testing for Refinery.
Alternative Monitoring for Wet Scrubber.
Alternative Timeline to Correct Exceedances at Landfill Well.
Alternative Timeline to Correct Exceedances at Landfill Well.
Alternative Monitoring for Vapors from Disulfide Separator Venting.
Preparatory Processes for Gypsum Stucco Production.
Alternative Timeline to Correct Exceedances at Landfill Well.
Alternative Timeline to Correct Exceedances at Landfill Well.
Alternative Timeline to Correct Exceedances at Landfill Well.
Alternative Timeline to Correct Exceedances at Landfill Wells.
Alternative Timeline to Correct Exceedances at Landfill Well.
Alternative Temperature at Recycling and Disposal Facility.
Alternative Temperature at Recycling and Disposal Facility.
Alternative Timeline to Correct Exceedances at Landfill Well.
Alternative Monitoring Procedures at a Landfill.
Alternative Timeline to Correct Exceedance at Landfill Well.
Alternative Timeline to Correct Exceedance at Landfill Well.
Alternative Monitoring, Testing, and Other Requirements for a Landfill.
Treated Landfill Gas Exemption.
Alternative Timeline to Correct Exceedance at Landfill Well.
Revision of Custom Fuel Monitoring Schedule.
Emissions Rate Reporting Requirements at Landfill.
Applicability Determination for Kraft Pulp Mill TRS Emissions.
Performance Testing Requirement Condition D.4.6.
Installation of a Capacitor/Reactor at an Electric Arc Furnace.
Alternative Monitoring for Opacity Due to Wet Gas Scrubber.
Alternative Timeline to Correct Exceedance at a Landfill Well.
Alternative Timeline to Correct Exceedance at a Landfill Well.
Landfill Gas Treatment Exemption.
Alternative Monitoring for Thermal Vapor Incinerator.
Alternative Monitoring Plan for Propane Vapor from a Vent Gas Absorber.
Alternative Monitoring Request for FCCU COMS at a Refinery.
Applicability for Co-Located Grain Elevators.
Alternative Testing Method Request for Wallboard Shredder.
Alternative Timeline to Correct Exceedance at a Landfill Well.
Change to Standard Operating Procedure at a Landfill.
Applicability for Sulfuric Acid Plants with Hydrogen Sulfide Burning Processes.
Compliance with ACGIH Ventilation Manual.
Clean Charge Defined.
Applicability to a Refinery Flare.
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Federal Register / Vol. 73, No. 251 / Wednesday, December 31, 2008 / Notices
80395
ADI DETERMINATIONS UPLOADED ON DECEMBER 12, 2008—Continued
Control number
Category
Subpart
Title
ADI Determinations Uploaded on December 23, 2008
0800089 ............
0800090 ............
Z080005 ............
NSPS ........
NSPS ........
NESHAP ...
Db ........
J, Ja .....
CC ........
Dryers at OSB Bark Burner System.
Integrated Gasification Combined Cycle Power Plant.
Integrated Gasification Combined Cycle Power Plant.
Abstracts
Abstract for [A080001]
Q: Does EPA allow ConocoPhillips’
Wood River Refinery in Roxana, Illinois,
to monitor the liquid benzene at the
finished product tanks under 40 CFR
part 60, subpart J, in lieu of
continuously monitoring the sulfur
dioxide concentration of the displaced
barge vapors from benzene loading?
These displaced barge vapors are
directed to the Marine Vapor Control
system thermal oxidizer.
A: Yes. EPA finds that the proposed
alternative monitoring proposal from
ConocoPhillips meets the requirements
of EPA’s guidance entitled ‘‘Alternative
Monitoring Plan for NSPS subpart J
Refinery Fuel Gas.’’ The displaced
benzene vapors from the benzene
loading are inherently low in sulfur
content.
pwalker on PROD1PC71 with NOTICES
Abstract for [M080005]
Q: Does EPA consider, as force
majeure, certain furnace malfunctions
and labor strikes that prevented stack
tests from being conducted before the
compliance deadline under 40 CFR part
63, subpart EEEEE, at the Indianapolis
Casting facility in Indianapolis, Indiana?
A: Yes. EPA finds that the certain
events, such as furnace malfunctions
and labor strikes, as described in EPA’s
response to Indianapolis Casting, can be
considered as force majeure under
MACT subpart A. The furnace
malfunctions were safety related and
required extended furnace shut downs
for repair, and labor actions are beyond
the control of the company.
Abstract for [M080006]
Q: Does EPA accept stack test results
performed before the compliance
deadline of 40 CFR part 63, subpart
EEEEE, as the required initial
compliance demonstration at the
Indianapolis Casting facility in
Indianapolis, Indiana?
A: Yes. EPA accepts stack test results
before the compliance deadline under
MACT subpart EEEEE as the initial
compliance demonstration only if the
production rates achieved during the
April 2005 tests are representative of the
highest production rates currently
achievable, and the gas sample volume
VerDate Aug<31>2005
17:41 Dec 30, 2008
Jkt 217001
collected meets or exceeds 60 dry
standard cubic feet for each sampling
run as specifically required under 40
CFR 63.7732(b)(2).
Abstract for [M080007]
Q: Does EPA allow S.D. Warren to
monitor the flue gas temperature of the
wet scrubber outlet in lieu of monitoring
the pressure drop across the wet
scrubber under 40 CFR part 63, subpart
DDDDD? The S.D. Warren Company/
SAPPI Fine Paper of North America’s
Skowhegan, Maine, pulp mill has a
large multi-fuel boiler with an
associated wet scrubber that does not
experience a significant pressure drop
because it is an open vessel.
A: Yes. EPA finds this acceptable
under MACT subpart DDDDD. A
temperature drop in the range of 250
degrees Fahrenheit at the scrubber
outlet will indicate that the flue gases
are coming into contact with the
scrubber water in order to control
particulate matter emissions. A
continuous monitoring system that can
be used to determine and record the flue
gas temperature of the boiler wet
scrubber outlet at least once every
successive 15-minute period should be
installed, calibrated, maintained, and
operated.
Abstract for [M080008]
Q: What are the applicability and
control requirements under 40 CFR part
63, subpart YY, for the plant exhaust
from the primary bag filter vents for
Units 1, 2, and 3 at the Sid Richardson
Big Springs facility in Howard County,
Texas, which are primarily routed to a
cogeneration unit but also can be routed
away from the facility’s cogeneration
unit to a flare?
A: The facility would be subject to
different requirements under MACT
subpart YY depending upon the use of
the exhaust gas. When the facility routes
the exhaust gas to the cogeneration unit,
no control requirements would apply.
During the times the facility bypasses
the cogeneration system to the flare, the
plant exhaust from the primary bag filter
vents for Units 1, 2, and 3 must meet the
requirements under MACT subpart YY
for process vents, unless there is a
startup, shutdown, or malfunction
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Sfmt 4703
(SSM). When the plant exhaust from the
primary bag filter vents for Units 1, 2,
and 3 bypasses the cogeneration unit
during SSM, the facility must follow its
SSM plan.
Abstract for [M080009]
Q: Does 40 CFR part 63, subpart IIIII
require a daily average or an hourly
average to determine continuous
compliance with the emissions standard
for mercury recovery units under
Section 63.8190(a)(3)?
A: When determining continuous
compliance with the emissions standard
for mercury recovery units under 40
CFR 63.8190(a)(3), a facility should
calculate a daily average mercury
concentration, using Equation 2 at 40
CFR 63.8240(a).
Abstract for [M080010]
Q: Does the exemption from the
definition of ‘‘organic liquid’’ for
gasoline (including aviation gasoline),
kerosene (No. 1 distillate oil), diesel
(No. 2 distillate oil), asphalt, and
heavier distillate oils and fuel oils in 40
CFR 63.2406 of the Organic Liquid
Distribution National Emissions
Standard for Hazardous Air Pollutants
(NESHAP), 40 CFR part 63, subpart
EEEE (OLD MACT) include the use of
toluene as a fuel in the inorganic
chemical process that manufactures
titanium dioxide (TiO2) at the DuPont
Company (DuPont) of Wilmington,
Delaware?
A: No. EPA concludes that the OLD
MACT applies to the storage and
transfer of toluene used as fuel in the
production of TiO2. The exemption in
40 CFR 63.2406(3)(i) in the definition of
‘‘organic liquid’’ applies only to those
expressly listed liquids. Because toluene
is an organic liquid and is not gasoline,
kerosene, diesel, asphalt, or a heavier
distillate oil or fuel oil, it is not eligible
for the exemption under 40 CFR
63.2406(3)(i) merely because it may be
used as a fuel.
Abstract for [M080011]
Q: Does EPA allow a facility to use
multiple standard batches to define a
process within a single miscellaneous
chemical manufacturing process unit
(MCPU) under 40 CFR part 63, subpart
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FFFF, National Emission Standards for
Hazardous Air Pollutants:
Miscellaneous Organic Chemical
Manufacturing (the MON rule)?
A: EPA finds that a facility may
request that EPA exercise its authority
under 40 CFR 63.10(f) to modify the
recordkeeping and reporting
requirements in the MON rule and
allow multiple standard batches per
process. Facilities can request approvals
of alternative recordkeeping and
reporting in their precompliance
reports. [See 40 CFR 63.2520(c)].
Alternatively, requests submitted after
the due date of the precompliance
report (i.e., after November 13, 2007)
may be submitted under 40 CFR
63.10(f).
Abstract for [M080012]
Q1: Which Standard Industrial
Classification (SIC) code applies to the
glucosamine hydrochloride production
process at Cargill Incorporated in
Eddyville, Iowa?
A1: The appropriate SIC code for the
glucosamine hydrochloride production
process is 289, Miscellaneous Chemical
Products.
Q2: Is the process subject to 40 CFR
part 63, subpart FFFF, the National
Emission Standards for Hazardous Air
Pollutants: Miscellaneous Organic
Chemical Manufacturing (MON) Rule?
A2: Yes. The glucosamine
hydrochloride production process is
subject to the MON Rule.
Q3: If this process is not subject to the
MON Rule, is it subject to the
Pharmaceuticals NESHAP or another
NESHAP?
A3: No, the facility is not subject to
the Pharmaceuticals NESHAP or
another NESHAP.
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Abstract for [M080013]
Q. Is the process by which the
Spartech Polycast facility in Stamford,
Connecticut, manufactures poly methyl
methacrylate (PMMA) acrylic sheet
subject to 40 CFR part 63, subpart FFFF?
A. Yes. Spartech’s operations produce
a material (PMMA) classified using
Standard Industrial Classification (SIC)
code 282 or The North American
Industry Classification System (NAICS)
NAICS code 325, and its operations
meet all the other criteria for MACT
subpart FFFF to apply.
Abstract for [M080014]
Q: Does EPA approve the use at Dow
Chemical’s Midland, Michigan, facility
of the results of performance tests
conducted on three thermal treatment
units under 40 CFR part 63, subparts
GGG and MMM, in lieu of conducting
an initial compliance demonstration for
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40 CFR part 63, subpart FFFF (the
MON)?
A: Yes. EPA approves the use of these
previously conducted performance tests
as the initial compliance demonstration
for the MON, based in part on Dow
Chemical’s use of test methods
referenced in MACT subpart FFFF and
its declaration that no significant
process changes have occurred since
these tests.
Abstract for [M080016]
Q1: Does EPA approve Dow
AgroSciences’ (DAS) request to monitor
the liquid temperature of its condensers
at its Harbor Beach, Michigan, facility as
an alternative to measuring the exhaust
gas temperature when demonstrating
initial compliance with 40 CFR part 63,
subpart GGG (the Pharma-MACT)?
A1: No. In regards to the initial
compliance demonstration for process
condensers under MACT subpart GGG,
EPA will not approve DAS’s request to
monitor the liquid temperature as an
alternative to monitoring the exhaust
gas temperature because DAS started
operating its condensers before the
compliance date, and it did not present
sufficient technical justification for the
alternative method.
Q2: Does EPA approve DAS’s request
to comply with the 20 ppmv outlet
concentration limit under
§ 63.1254(a)(1)(ii)(A) without
calculating uncontrolled hazardous air
pollutant emissions from all emission
episodes using the equations specified
in § 63.1257(d)(2)(i), or developing an
engineering assessment as allowed in
Section 63.1257(d)(2)(ii), or developing
an emission profile as required by
§ 63.1257(b)(8)(ii)?
A2: No. In regards to complying with
the 20 ppmv outlet concentration limit
under 40 CFR 63.1254(a)(1)(ii)(A), EPA
will not approve DAS’s request to forgo
calculating uncontrolled emissions,
developing an engineering assessment,
or developing an emission profile
because the alternative standard, at
§ 63.1254(c), is the only process-vent
compliance option for the PharmaMACT that does not require calculation
of uncontrolled emissions because it
requires continuous monitoring through
a continuous emission monitoring
system (CEMS). As DAS does not
employ a CEMS, the only way it can
ensure compliance with 40 CFR
63.1254(a)(1)(ii)(A) is if it calculates
uncontrolled emissions and develops an
emission profile under worst-case
conditions.
Abstract for [M080017]
Q: Does EPA approve at Dow
Chemical Company’s Midland,
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Michigan, facility, the use of the results
of performance tests conducted on three
thermal treatment units per 40 CFR part
63, subparts GGG and MMM, in lieu of
conducting an initial compliance
demonstration for 40 CFR part 63,
subpart FFFF (the MON)?
A: Yes. EPA approves the use of these
previously conducted performance tests
as the initial compliance demonstration
for the MON, based on Dow’s use of test
methods referenced in 40 CFR part 63,
subpart FFFF and statement that no
significant process changes have
occurred since these tests.
Abstract for [M080018]
Q: Does EPA approve alternative test
methods, monitoring, and work practice
standards under 40 CFR part 63, subpart
N, for Finishing Innovation’s proposed
new hard chrome electroplating tank in
Warsaw, Indiana? The proposed new
tank will be equipped with an Emission
Elimination Device (EED), or formerly
known as the Merlin Cover, which is a
patented system which totally encloses
the chrome tank while plating takes
place.
A: Yes. EPA approves the proposed
alternative test method, monitoring
procedures and work practices
consistent with previous approvals.
EPA’s Office of Air Quality Planning
and Standards (OAQPS) approved an
alternative test method utilizing a
smoke generation device. This device
would be ignited and placed inside the
EED and the absence of leaking smoke
confirmed to demonstrate that the EED
completely encloses the atmosphere
over the chrome electroplating tank.
EPA Region 5 has also approved
alternative monitoring requirements and
work practices to monitor continuous
compliance of the EED and to ensure
that it maintains compliance.
Abstract for [M080019]
Q: Does J.L. French Corporation’s
variance request letter contain adequate
information for the EPA to approve a
request for waiver of initial performance
tests as well as all subsequent
performance tests for the existing
aluminum scrap shredders located at
J.L. French Corporation’s Gateway and
Taylor secondary aluminum production
facilities in Sheboygan, Wisconsin?
A: No. EPA finds that based on the
information submitted to the EPA, we
cannot approve J.L. French
Corporation’s request for waiver of
initial performance tests, as well as all
subsequent performance tests for the
existing aluminum scrap shredders. For
the EPA to make an informed decision
either approving or denying such a
request, J.L. French Corporation’s
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application for waiver of performance
tests must be accompanied by a
comprehensive compliance status report
proving compliance with the relevant
aluminum scrap shredder standards at
40 CFR part 63, subpart RRR. In
addition, 40 CFR 63.7(h)(3)(iii) provides
that any application for a waiver of a
performance test shall include
information justifying the owner or
operator’s request for a waiver, such as
the technical or economic infeasibility,
or the impracticality, of the affected
source performing the required test.
Abstract for [M080020]
Q: Does EPA approve a change to
Viscofan’s (formerly Teepak) alternative
monitoring plan under 40 CFR part 63,
subpart UUUU, originally approved in
February 2005 at its facility in Danville,
Illinois? Viscofan would like to replace
one of its GC/PID instruments with a
new Baseline-MOCON, Incorporated
Model 8900 GC/PID to measure
hydrogen sulfide and carbon disulfide.
A: Conditional. EPA has determined
that it is acceptable under MACT
subpart UUUU for Viscofan to perform
a carrier gas (zero) and a single upscale
gas Quality Control (QC) check on a
daily basis for each chemical monitored.
However, Viscofan must still do a full
linearity-type calibration (zero and at
least three upscale gas concentrations)
initially and at least quarterly thereafter
for each chemical monitored.
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Abstract for [Z080003]
Q: Does EPA allow modification in
the existing vinyl chloride alternative
monitoring plan under 40 CFR part 61,
subpart F, for Lubrizol Advanced
Material’s polyvinyl chloride plant in
Louisville, Kentucky?
A: Yes. Based upon a statistical
analysis presented by Lubrizol, EPA
finds that there are only minor
differences between individual and
composite resin samples that the
company analyzes on a monthly basis
under NESHAP subpart F. Therefore,
EPA waives the requirement to compare
the results of individual and composite
samples on a monthly basis.
Abstract for [0800017]
Q: Does EPA approve an alternative
opacity monitoring procedure, which
consists of monitoring the secondary
power input to the electrostatic
precipitator (ESP), for a boiler at the
U.S. Sugar facility in Clewiston, Florida,
which is subject to 40 CFR part 60,
subpart Db?
A: No. Because NSPS subpart Db was
modified to allow the use of a
particulate matter continuous emission
monitoring system (PM CEMS) as an
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alternative to the use of a continuous
opacity monitoring system (COMS),
EPA finds that there is no justification
for now allowing the use of parametric
monitoring of the ESP. Therefore, unless
U.S. Sugar can demonstrate that a PM
CEMS is not a viable alternative to a
COMS, EPA does not approve the
request to use parametric monitoring,
which is a less accurate and reliable
alternative.
Abstract for [0800018]
Q: Does EPA approve changes to
monitoring and operational
requirements for the landfill operated by
Environtech in Morris, Illinois, under 40
CFR part 60, subpart WWW?
A: Conditional. EPA finds that it
needs to approve alternatives to
monitoring and operational
requirements that are part of the design
plan, and EPA’s Office of Air Quality
Planning and Standards (OAQPS)needs
to approve such alternative test
methods. However, the Illinois
Environmental Protection Agency
(IEPA) has the authority to approve nonmonitoring, non-operational changes to
the design plan. EPA refers to several
previous determinations on the
Applicability Determination Index (ADI)
with ADI Control Numbers 03000120,
0400033, 0600062, 0600063, and
M040028, and the modifications of
September 21, 2006, to 40 CFR part 60
(71 FR 55127) in addressing many
specific requests.
Abstract for [0800019]
Q: Does EPA approve changes to
monitoring and operational
requirements for the landfill operated by
LandComp in Ottawa, Illinois, under 40
CFR part 60, subpart WWW?
A: Conditional. EPA finds that it
needs to approve alternatives to
monitoring and operational
requirements that are part of the design
plan, and EPA’s Office of Air Quality
Planning and Standards (OAQPS)
specifically within EPA needs to
approve alternative test methods.
However, the Illinois Environmental
Protection Agency (‘‘IEPA’’) has the
authority to approve non-monitoring,
non-operational changes to the design
plan. EPA refers to a several previous
applicability determinations on the
Applicability Determination Index (ADI)
with ADI Control Numbers 03000120,
0400033, 0600062, 0600063, and
M040028, and the modifications of
September 21, 2006, to part 60 (71
Federal Register 55127) in addressing
many specific requests.
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80397
Abstract for [0800020]
Q: Does EPA approve changes to
monitoring and operational
requirements for the landfill operated by
Lee County in Dixon, Illinois, under 40
CFR part 60, subpart WWW?
A: Conditional. EPA finds that it
needs to approve alternatives to
monitoring and operational
requirements that are part of the design
plan, and EPA’s Office of Air Quality
Planning and Standards (OAQPS) needs
to approve alternative test methods.
However, IEPA has the authority to
approve non-monitoring, nonoperational changes to the design plan.
EPA refers to several previous
applicability determinations on the
Applicability Determination Index (ADI)
with ADI Control Numbers 03000120,
0400033, 0600062, 0600063, and
M040028, and the modifications of
September 21, 2006, to part 60 (71 FR
55127) in addressing many specific
requests.
Abstract for [0800021]
Q: Does EPA allow the gas-fired
process heater (new 77F–1) installed at
the Marathon Ashland Petroleum
refinery (Marathon) in Robinson,
Illinois, to be exempt from 40 CFR part
60, subpart Ja, given that the heater was
purchased in 2001 but never installed?
A: No. Given the six-year gap since
the purchase of the heater and its
incomplete fabrication, and given
further that Marathon has not started the
bidding process to ship and install the
process heater, EPA finds that Marathon
has not undertaken a continuous
program of construction and has not
‘‘commenced construction’’ of an
‘‘affected facility’’ on or prior to May 14,
2007. Thus, when the heater is
constructed at the refinery and upon the
effective date of NSPS subpart Ja, the
heater will be subject to NSPS subpart
Ja.
Abstract for [0800022 & 0800023]
Q: Does EPA allow the Milam
Recycling and Disposal facility (Milam)
in East Street Louis, Illinois, to obtain a
higher operating temperature for landfill
gas extraction wells MW 39 and MW58
under 40 CFR part 60, subpart WWW?
A: Yes. The NSPS requires that each
interior wellhead in the collection
system operate with a landfill gas
temperature less than 131 degrees
Fahrenheit. The facility may request a
higher operating temperature under
NSPS subpart WWW if supporting data
demonstrate that the elevated
temperature does not cause fires or
inhibit anaerobic decomposition by
killing methanogens. As Milam has
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submitted such data, EPA approves a
higher operating temperature of 140
degrees Fahrenheit for well MW39 and
MW58.
Abstract for [0800024]
Q: Does EPA approve an alternative
timeline, under 40 CFR part 60, subpart
WWW, to correct oxygen exceedances at
leachate cleanout riser LCO–02A at the
Veolia Orchard Hills Landfill in Davis
Junction, Illinois?
A: Yes. EPA approves the alternative
timeline under NSPS subpart WWW.
Veolia Orchard Hills Landfill may have
until 45 days of the initial exceedance
to correct the oxygen exceedances.
Abstract for [0800025]
Q: Does EPA allow the OwensBrockway Glass Container facility in
Lapel, Indiana, to measure the
bridgewall optical temperature (BWOT),
under 40 CFR part 60, subpart CC, three
times per shift instead of installing and
operating a continuous opacity monitor
on its Furnace Number 32?
A: No. NSPS subpart CC requires that
continuous parameter monitoring
systems complete a minimum cycle of
operation (sampling, analyzing and data
recording) every 15 minutes. EPA
determines that if the BWOT cannot be
measured continuously, then it is not an
appropriate alternative monitoring
parameter to opacity, and the facility
should install a COM.
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Abstract for [0800026]
Q: Does EPA approve an alternative
timeline under 40 CFR part 60, subpart
WWW, to correct oxygen exceedances at
Veolia’s Valley View Landfill in
Decatur, Illinois?
A: Yes. EPA approves an extension of
up to 53 days from the date of the initial
exceedance to bring wells 19R and 26R
into compliance with the oxygen
concentration standard under NSPS
subpart WWW.
Abstract for [0800027]
Q1: Does EPA consider indirect-fired
dryers used in the ethanol industry
subject to 40 CFR part 60, subparts Db
or Dc?
A1: EPA finds that both NSPS
subparts Db and Dc apply to indirectfired dryers as they use the process of
drying in a closed steam loop system
with an integrated thermal oxidizer to
transfer heat across a physical barrier. In
the indirect heating method being used,
they meet the definition of a steam
generating unit under 40 CFR 60.41b
and 60.41c.
Abstract for [0800028]
Q1: Does EPA considered any of the
material used as a feedstock on the
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Spherical Catalyst Manufacturing (SCM)
Line 1 at UOP’s Shreveport, Louisiana,
plant, a ‘‘mineral’’ as term is used in the
definition of ‘‘mineral processing
plant,’’ under NSPS subpart UUU?
A1: No. EPA finds that none of the
feed materials used on SCM Line 1
(pure aluminum, hydrochloric acid,
and/or aluminum hydroxychloride
solution) is a ‘‘mineral,’’ as the term is
used in the definition of ‘‘mineral
processing plant,’’ under at 40 CFR
60.731.
Q2: Does synthetic alumina produced
on the Spherical Catalyst Manufacturing
(SCM) Line 1 at UOP’s Shreveport,
Louisiana, plant, using a combination of
pure aluminum, hydrochloric acid, and/
or aluminum hydroxychloride solution,
meet the definition of a ‘‘mineral,’’ as
the term is used in NSPS CFR subpart
UUU in the definition of the affected
facility: each calciner and dryer at a
‘‘mineral processing plant,’’ located in
NSPS subpart UUU at 40 CFR 60.730?
A2: No. EPA finds that the synthetic
alumina produced on SCM Line 1 does
not meet the definition of ‘‘mineral.’’
Q3: Is SCM Line 1, located at UOP’s
Shreveport, Louisiana, plant, processing
a ‘‘mineral,’’ as the term is used in 40
CFR part 60, subpart UUU, or producing
a ‘‘mineral,’’ as the term is used in the
definition of the affected facility (each
calciner and dryer at a ‘‘mineral
processing plant’’) in subpart UUU,
potentially subject to NSPS part 60,
subpart UUU?
A3: No. EPA finds that SCM Line 1
cannot be subject to subpart UUU,
because it neither processes a
‘‘mineral,’’ nor does it produce a
‘‘mineral,’’ and, therefore, it does not
meet the NSPS subpart UUU definition
of a ‘‘mineral processing plant’’
Abstract for [0800029]
Q: Does EPA allow Louisville Gas and
Electric (LG&E) to substitute particulate
matter continuous emission monitoring
systems (PM CEMS) for continuous
opacity monitoring systems (COMS)
under 40 CFR part 60, subpart D, on
Units 3 and 4 at its Mill Creek Station
in Louisville, Kentucky?
A: Yes. Because EPA believes that PM
CEMS will be superior to COMS for
verifying compliance with the
applicable particulate emission limit for
Units 3 and 4, LG&E’s alternative
monitoring proposal under NSPS
subpart D is approved, provided that a
number of conditions outlined in the
approval are met.
Abstract for [0800030]
Q: Does EPA allow the Kentucky
Utilities Company (KU) to substitute
particulate matter continuous emission
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monitoring systems (PM CEMS) for
continuous opacity monitoring systems
(COMS) under 40 CFR part 60, subpart
D, on Unit 3 at its Mill Ghent Station in
Ghent, Kentucky?
A: Yes. Because EPA believes that PM
CEMS will be superior to COMS for
verifying compliance with the
applicable particulate emission limit
under NSPS subpart D for Unit 3, EPA
approves KU’s alternative monitoring
request, provided that a number of
conditions outlined in the EPA response
are met.
Abstract for [0800031]
Q: Does the replacement of the gas
turbine at the Bristol-Myers Squibb
facility in New Brunswick, New Jersey,
constitute reconstruction under 40 CFR
part 60, subpart KKKK?
A: Conditional. For the purpose of
NSPS subpart KKKK, EPA finds that the
affected facility is not limited to the
turbine itself. It is not clear from the
submittal what the fixed capital cost of
the new components is as compared to
a similar entirely new facility. Costs
outside of the affected facility, such as
the building, air pollution control,
testing, and monitoring equipment, site
preparation, removal of the old turbine,
and contingency costs should not be
included.
Abstract for [0800032]
Q: Does EPA approve the use of
sensory means (i.e., visual, audible, or
olfactory), as an alternative, under 40
CFR part 60, subparts VV and VVa, to
using EPA Method 21 for the
identification of leaks from equipment
in acetic acid service at the Eastman
Chemical Company facility in
Columbia, South Carolina?
A: Yes. EPA finds that the proposed
alternative is acceptable under NSPS
subparts VV and VVa. Monitoring
results provided by Eastman indicate
that leaks from equipment in acetic acid
service are more easily identified
through sensory methods than by using
Method 21 because of the physical
properties (high boiling point, high
corrosivity, and low odor threshold) of
acetic acid and the process conditions at
the plant.
Abstract for [0800033]
Q: May Air Products and Chemicals,
Inc. (Air Products) use the process
monitor as the primary method to
measure hydrogen sulfide (H2S) for two
furnaces located within the ExxonMobil
Joliet, Illinois, refinery, and eliminate
the previously stipulated alternative
monitoring plan (AMP) conditions that
require random H2S grab sampling,
under the New Source Performance
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Standards for Petroleum Refineries, 40
CFR part 60, subpart J.
A: No. EPA finds that the conditions
of the AMP cannot be revised, because
monitoring a process parameter is not a
substitute for H2S grab sampling. Please
refer to a previous EPA approved AMP
available on the Applicability
Determination Index (AD)) under ADI
Control Number 0100037.
Abstract for [0800034]
Q: Does EPA approve a boiler derate
proposal , under 40 CFR part 60, subpart
Dc, based on changes made to the
natural gas-fired boiler at the facility
located in Dearborn, Michigan?
A: Yes. EPA approves this proposal
under NSPS subpart Dc, as it will
reduce the capacity of the boiler and
will comply with EPA’s policy on
derates.
Abstract for [0800035]
Q: Does EPA approve an alternative
compliance timeline under 40 CFR part
60, subpart WWW, to correct a pressure
exceedance at the Livingston Landfill,
Well GW10, located in Pontiac, Illinois?
A: No. On November 20, 2007, the
GW10 well at Livingston Landfill
showed a positive pressure reading. On
December 3, 2007, Livingston requested
an extension to bring the well into
compliance. However, according to a
phone conversation between EPA and
Cornerstone Environmental Group on
January 4, 2008, the well had achieved
compliance within 15 days of the initial
exceedance. Therefore, EPA determines
that an alternative compliance timeline
was not required.
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Abstract for [0800036]
Q: Does EPA concur with Michigan
Consolidated Gas Company (MichCon),
a solely owned subsidiary of DTE
Energy LLC, that 40 CFR part 60,
subpart KKK, does not apply to the
recent expansion project of a propane
refrigeration plant at MichCon’s Belle
River Mills facility?
A: No. EPA determines that NSPS
subpart KKK is applicable to the recent
expansion project because the propane
refrigeration system uses a process that
extracts ‘‘natural gas liquids.’’ Thus, the
facility meets the definition of a natural
gas processing plant set forth in 40 CFR
60.631.
Abstract for [0800037]
Q: Does EPA approve an alternative
monitoring plan, under 40 CFR part 60,
subpart UUU, to monitor the nozzle
pressure of a Venturi scrubber instead of
the pressure loss of the gas stream
through the Venturi scrubber at 3M’s
Cottage Grove, Minnesota, facility?
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A: Yes. EPA finds that the 3M
Company has demonstrated that the
nozzle pressure is a reasonable
alternative under NSPS subpart UUU to
the pressure loss of the gas stream
through the Venturi scrubber.
Abstract for [0800038]
Q: Does EPA approve an alternative
timeline under 40 CFR part 60, subpart
WWW, to correct oxygen exceedances at
Veolia Orchard Hills Landfill’s Leachate
Recirculation Line LRW–12, located in
Davis Junction, Illinois?
A. Yes. On February 14, 19, and 26,
2008, Veolia’s leachate recirculation
line, LRW–12, exceeded the 5 percent
oxygen concentration standard. EPA
approved an alternate timeline under
NSPS subpart WWW for Veolia to
correct the oxygen exceedances until
May 14, 2008. EPA finds that if the
oxygen standard cannot be met by May
14, 2008, the landfill will need to apply
to have the well decommissioned. If
Illinois EPA does not approve such
decommissioning, and Veolia cannot
achieve an oxygen concentration below
5 percent by May 14, 2008, then Veolia
must have the gas collection system
expanded by 120 days of the initial
exceedance.
Abstract for [0800039]
Q: Does EPA approve an alternative
timeline under 40 CFR part 60, subpart
WWW, for Roxana Landfill, in Roxana,
Illinois, to correct positive pressure at
the wells number 6, 7, 8, 18, 20, 22, 23,
24, 38, 39, 40, 41, 42, 43, 44, 45, and 46
wells?
A: Yes. EPA approves Roxana’s
proposed alternative timeline under
NSPS subpart WWW. However, if
Roxana cannot measure and achieve
negative pressure without excess air
infiltration at the wells number 6, 7, 8,
18, 20, 22, 23, 24, 38, 39, 40, 41, 42, 43,
44, 45, and 46 by the alternative
compliance date, Roxana must expand
the gas collection system within 120
days of the initial exceedances.
Abstract for [0800040]
Q: Does EPA approve alternative
operational standards and procedures
under 40 CFR part 60, subpart WWW,
for oxygen/pressure for six low gas
producing wells at Veolia
Environmental Services’ Zion Landfill
in Zion, Illinois?
A: Yes. EPA approves adjusted
standards and procedures under NSPS
subpart WWW for oxygen and pressure
for low gas producing extraction points
where gas flows are so low that applying
even minimal vacuum results in
exceedances of the applicable oxygen
concentration limit and the persistent
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oxygen/pressure exceedances are not
due to operational or maintenance
issues. Instead of decommissioning or
permanently disconnecting such
extraction locations, which would result
in no gas control, it is better to keep
operating them and allow the locations
to remain shut off, under positive
pressure, with monthly monitoring and
periodic adjustment to vacuum to
remove accumulated landfill gas.
Abstract for [0800041]
Q1: Do the process and alcohol day
tanks at Archer Daniels Midland’s
(ADM) dry mill ethanol production
facility at its existing corn wet mill in
Columbus, Nebraska, meet the process
tank definition which exempts them
from the control requirements of 40 CFR
part 60, subpart Kb?
A1: Yes. EPA finds that these tanks
are used within the process, are process
tanks, and are not considered storage
vessels subject to NSPS subpart Kb
Q2: Is the alcohol QC tank also a
process tank and not a storage vessel
under NSPS subpart Kb?
A2: No. EPA finds that this tank does
not engage in the type of unit operations
or other functions described for process
tanks, and is outside of the process. The
sampling performed at the tank does not
qualify this tank as a process tank. It is
subject to NSPS subpart Kb as a storage
vessel.
Q3: Is the alcohol reclaim tank a
process tank and not a storage vessel
under NSPS subpart Kb?
A3: No. EPA finds that this tank
serves as a feed vessel for reintroduction
of material back into the process. It is
not within the process, and is a storage
vessel subject to NSPS subpart Kb.
Abstract for [0800042]
Q: Does EPA rescind two
determinations posted to the
Applicability Determination Index (ADI)
with ADI Control Numbers 0400015 and
0500014 regarding modification of
storage tanks due to storage of gasoline
under 40 CFR part 60, concerning which
the American Petroleum Institute (API)
believes the sources are exempt?
A: No. EPA finds that the facilities at
issue are not facilities owned or
operated by API, and reconsideration of
one of the determinations has already
been requested by the source owner/
operator and is being addressed by the
Agency.
Abstract for [0800043]
Q: For Missouri River Energy
Services’ (MRES) facility in Audubon,
Iowa, does EPA consider the
manufacturer the original owner or
operator of a stationary gas turbine
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under 40 CFR part 60, subpart GG, and
40 CFR part 60, subpart KKKK?
A: Conditional. EPA finds that it
depends on whether the entire affected
facility was completely manufactured
and fabricated by the manufacturer and
purchased in completed form. In the
analysis of this specific case, EPA
determined that the turbine
manufacturer was the original owner or
operator. However, it is not true as a
general matter that manufacturers of gas
turbines are always the original owners
or operators.
Abstract for [0800044]
Q1: Do physical changes to increase
the coal feed rate to maintain generating
capacity when switching coal type at
NRG Energy’s Indian River Generating
Station in Millsboro, Delaware,
constitute a modification of the boiler
under 40 CFR part 60, subpart Da?
A1: Yes. EPA finds that physical
changes to increase the coal feed rate
would enable an increase in kg/hr
emissions under NSPS subpart Da.
Q2: If the dedicated steam turbines
physically limit the amount of steam
that may be generated, does this prevent
the boiler from being modified?
A2: No. EPA finds that applicability is
determined based on the affected
facility alone. Changes made to a
downstream unit which is not part of
the affected facility do not affect
applicability of the boiler.
Abstract for [0800045]
Q: Does EPA consider the pressure
limitations on boilers at the NRG Energy
Indian River Generating Station in
Millsboro, Delaware, as a limiting factor
in the source’s ability to increase
emissions due to a proposed increase in
feed rate under 40 CFR part 60, subpart
Da?
A: EPA believes the proposed changes
could enable an increase in kg/hr
emissions under NSPS subpart Da.
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Abstract for [M080021]
Q: Does EPA waive the applicability
of 40 CFR 63.1511(e) for the aluminum
shredder/baler at the Alcoa facility in
Newburgh, Indiana, under MACT
subpart RRR?
A: No. EPA does not waive the
applicability of 40 CFR 63.1511(e),
including all monitoring and testing
requirements, to the aluminum
shredder/baler. EPA does not believe
the performance testing proposed by
Alcoa provides sufficient evidence for
the waiver because one test is
insufficient.
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Abstract for [M080022]
Q: Does EPA approve the alternative
monitoring request for the Cognis
facility in Kankakee, Illinois, under 40
CFR part 63, subpart NNNNN? The
facility requests approval to remove
scrubber effluent pH as one of the
monitoring parameters for a water
scrubber/mist eliminator.
A: Yes. EPA approves the alternative
monitoring plan requested by Cognis
under MACT subpart NNNNN. Cognis’s
water scrubber is a ‘‘once through’’
scrubber system, and the scrubber
always has enough absorptive capacity
for the CHI, regardless of the pH.
Abstract for [M080023]
Q: Does EPA approve the request from
Allied Metal Company (Allied), located
in Chicago, Illinois, to begin operation
of a thermal chip dryer, under 40 CFR
part 63, subpart RRR?
A: Conditional. EPA approves Allied’s
request under MACT subpart RRR, but
only if Allied operates the thermal chip
dryer and all associated emission
control equipment for performance test
preparation beginning in January 2007.
All performance testing must be
completed by March 1, 2007. If Allied
cannot follow this schedule, Allied
must cease operating the thermal chip
dryer and notify EPA.
Abstract for [M080024]
Q: How does EPA find that the
delisting of 2-butoxyethanol from the
list of hazardous air pollutants (HAPs)
affects the Hydrite Chemical Company
(Hydrite) in Oshkosh, Wisconsin, under
40 CFR part 63, subpart KKKK? The
facility had obtained permits to limit the
potential-to-emit of HAPs to less than 25
tons of all combined HAPs and less than
ten tons of any individual HAP.
A: EPA finds that if the permit limits
for Hydrite were federally enforceable
before the first major compliance date
for existing sources, which is November
13, 2006, the facility would be
considered a minor source for purposes
of MACT subpart KKKK applicability. If
the facility is subject to a MACT
standard for which the first major
compliance date has passed, the facility
remains subject to that standard,
regardless of any reduction in potential
emissions which may result from no
longer using the delisted HAP.
Abstract for [M080025]
Q: Does EPA approve the alternative
monitoring procedures at the Flint Hills
Resource’s Joliet Facility (Joliet) in
Joliet, Illinois, under 40 CFR part 63,
subpart G? The facility has requested to
reroute the emissions from a vent
header system to a vent condenser
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followed by a carbon adsorber system
for the maleic anhydride (MAN)
process. Instead of regenerating the
carbon adsorbers on site, FHR planned
to send the spent canisters off site.
A: Yes. Joliet’s June 20, 2006, request
amended the original request dated
October 3, 2005, stating that the carbon
canister system would contain 4 parallel
trains with two carbon canisters in
series, in addition to other details
sufficient for EPA’s approval. (See ADI
Control Number M080026.) Thus, per
the amendments in the June 20, 2006,
request, EPA approves the revised
alternative monitoring plan pursuant to
40 CFR 63.151(f).
Abstract for [M080026]
Q: May Flint Hills Resource, LP, at its
Joliet Facility in Joliet, Illinois, re-route
the emissions from a vent header system
to a vent condenser followed by a
carbon adsorber system for the maleic
anhydride (MAN) process and send the
spent canisters off site, under 40 CFR
part 63, subpart G?
A: No. EPA finds that this monitoring
method is insufficient for demonstrating
continuous compliance. Additionally,
there is no proposed backup system for
the ‘‘channel’’ analyzer in between the
carbon canisters in each canister train.
Finally, it is unclear exactly how many
carbon canisters will be included in the
proposed carbon adsorber system.
Abstract for [M080027]
Q: Does EPA waive the dioxin/furan
(D/F) performance testing on Furnaces 2
and 6 of Jupiter Aluminum Corporation
(Jupiter) in Hammond, Indiana, under
40 CFR part 63, subpart RRR? Jupiter
has provided the baghouse inlet and
outlet temperatures for both furnaces.
The inlet and outlet temperatures for the
baghouses on Furnaces 2 and 6 are
below 130 degrees F, the D/F formation
temperature.
A: Based on the information
submitted, EPA waives Jupiter’s
requirement to test Furnace 2 for D/F.
However, EPA believes for Furnace 6, a
hole may have been in the ductwork
during the testing on the old baghouse,
and Jupiter has not repaired the hole.
Therefore, at this time, EPA does not
waive the requirement to test Furnace 6
for D/F. (See also ADI Control Number
M080028.)
Abstract for [M080028]
Q1: Does EPA waive the dioxin/furan
(D/F) performance testing on Furnaces 2
and 6 of Jupiter Aluminum Corporation
(Jupiter) in Hammond, Indiana, under
40 CFR part 63, subpart RRR?
A1: No. EPA is clarifying that the
D/F test waiver provided to Jupiter for
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Furnace 2 by letter dated December 19,
2005, is rescinded. (See ADI Control
Number M080027.) Until Jupiter
conducts performance testing that
demonstrates compliance with 40 CFR
63.1515(i), EPA considers Jupiter to be
in continuous noncompliance which
may result in civil penalties under the
Clean Air Act. As previously stated in
EPA’s letter to Jupiter dated October 10,
2006, EPA views any previous testing
Jupiter conducted on Furnaces 2 and 6
as unreliable and unacceptable.
Q2: Does EPA approve the current
method Jupiter uses of weighing the
final end product instead of weighing
the scrap charged in each furnace under
40 CFR part 63, subpart RRR?
A2: No. EPA does not approve the
current method of weighing the final
end product. Jupiter must propose a
weighing plan that records the weight of
scrap charged in each furnace.
Q3: Does EPA approve the
intermittent lime injection schedule
used by Jupiter under 40 CFR part 63,
subpart RRR?
A3: No. EPA is clarifying that since
Jupiter has not demonstrated
compliance with the emission limits in
NESHAP subpart RRR through the
required compliance testing, EPA has
not approved the intermittent lime
injection schedule used by Jupiter.
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Abstract for [M080029]
Q: Does EPA approve the use of the
presence of a pilot flame as an
alternative monitoring parameter
(AMP), even without the use of assist
gas in the flare, at the Murphy Oil USA,
Incorporated refinery located in
Superior, Wisconsin, which operates a
gasoline loading rack subject to 40 CFR
part 63, subpart R and 40 CFR part 63,
subpart CC?
A: No. EPA determines that the data
presented by Murphy does not
adequately assure continuous
compliance sufficiently to allow for
pilot presence to be used in lieu of
control device temperature. The method
that Murphy plans to use to demonstrate
continuous compliance was not used
during the performance test, and we are
unable to determine if such AMP is
appropriate. In a previous
determination, EPA discussed a
proposed alternative monitoring
program for a thermal oxidizer system,
including the importance of flame
stability. (See ADI Control number
M000002 dated 10/05/1998.)
Abstract for [M080030] Deleted
Abstract
Abstract for [M080031]
Q: Nucor Sheet Mill Group of
Crawfordsville, Indiana, operates
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annealing furnaces, each consisting of
thirty (30) individual burners and Utubes. Under 40 CFR part 63, subpart
DDDDD, does EPA consider this as a
whole a ‘‘process heater,’’ or does it
consider each individual U-tube burner,
each exhausting through an individual
stack to the atmosphere, itself a
‘‘process heater’’?
A: EPA finds that the entire annealing
furnace, with all 30 U-tubes and
burners, is considered a single ‘‘process
heater’’ with respect to this rule. EPA
understands that each U-tube in a
furnace cannot operate individually,
because in order for the steel to be
heated evenly, all three main zones
must be used when operating.
Abstract for [M080034]
Q: Does EPA approve the waiver
request from United States Steel in
Granite City, Illinois, to test particulate
emissions from two argon stir stations
under 40 CFR part 63, subpart FFFFF?
A: Yes. EPA finds that the
justification for a waiver provided by
United States Steel under MACT
subpart FFFFF adequately demonstrates
the impracticability of testing the same
baghouse again during operation of only
the argon stir stations, and EPA
determines that it is within United
States Environmental Protection Agency
guidance regarding the granting of such
waivers.
Abstract for [M080035]
Q: Does EPA find that a performance
test can be used to demonstrate
compliance with the Paper and Other
Web Coating MACT under 40 CFR part
63, subpart JJJJ, at the Rollprint
Packaging Products, Inc. (Rollprint)
facility in Addison, Illinois?
A: Yes. EPA finds that the testing
demonstrates compliance with the
requirements of 40 CFR 63.3320(1).
Abstract for [Z080004]
Q: Does EPA find that the Mercury
NESHAP, under 40 CFR part 61, subpart
E, applies to the sludge dryer within a
wastewater pretreatment facility at the
Chem-Plate Industries facility, located
in Elk Grove Village, Illinois?
A: Yes. EPA finds that the Mercury
NESHAP applies to all sludge treatment
processes, regardless of process
location. The provision does not
provide for any special circumstances,
such as the size of the waste treatment
plant of likelihood of mercury in the
effluent.
Abstract for [0800046]
Q: Anheuser-Busch, Incorporated
receives barley by ship at its
Manitowoc, Wisconsin, malting facility
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80401
and unloads it by a self-unloading leg
that dumps the barley into a hopper
controlled by a flexible transition boot
covering the end of the ship’s selfunloading conveyor and the malt plant’s
grain receiving hopper. Does EPA
consider this adequate control for
particulate emissions under 40 CFR part
60 subpart DD?
A: No. EPA considers the entire selfunloading leg to be subject to the
requirements of 40 CFR part 60 subpart
DD. EPA finds that a flexible transition
boot will adequately control particulate
emissions from the end of the selfunloading leg and the grain receiving
hopper at least as well as the
requirements listed in 40 CFR
60.302(d)(1) and (d)(2). However, the
flexible transition boot does not control
emissions from the portion of the selfunloading leg that the boot does not
cover.
Abstract for [0800047]
Q: Does EPA approve a gas treatment
exemption for the Beecher Energy LLC
(Beecher) facility located in Beecher,
Illinois, under 40 CFR part 60, subpart
WWW? Beecher uses landfill gas as a
fuel to power internal combustion
engines for electricity generators.
A: EPA finds that pursuant to 40 CFR
60.752(b)(2)(iii), collected landfill gas is
required to be routed to a control system
that complies with the requirements in
either an open flare or a control system
or enclosed combustor designed to
reduce nonmethane organic compounds
(NMOC), or a treatment system that
processes the collected gas for
subsequent sale or use. The landfill gas
applicable to Beecher has been treated
for sale or use. Once the landfill gas is
treated, such facilities that buy or use
the gas have no further associated
obligations in regards to the NSPS
subpart WWW.
Abstract for [0800048]
Q: British Petroleum Whiting
Business Unit (BP) requests a review of
an alternative monitoring plan (AMP) to
the New Source Performance Standards
for Petroleum Refineries at 40 CFR part
60, subpart J for its Beavon Stretford
Tail Gas Treatment unit. May BP
mathematically calculate the expected
sulfur dioxide (SO2) concentration using
the existing TRS measurements and
equation 15–2 in Method 15 rather than
physically converting the total reduced
sulfur (TRS) compounds and then
measuring the SO2 with a continuous
emissions monitor (CEM) following
Method 15A as specified in 40 CFR part
60, Appendix A?
A: Yes. EPA approves this change
because this monitoring method is
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consistent with the provisions of NSPS,
subpart J. The SO2 concentration
calculated above must comply with the
250 parts per million limit established
in 40 CFR 60.105(a)(7)(ii).
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Abstract for [0800049]
Q: May British Petroleum Products
North America, Incorporated (British),
Whiting Business Unit in Whiting,
Indiana, use fourteen hydrogen sulfide
grab samples of loading rack emissions
in lieu of installing a continuous
emission monitoring system (CEM) as is
required by 40 CFR part 60, subpart J
(NSPS subpart J) for a vapor combustion
unit (VCU)?
A: Yes. Based upon the information
provided by British, EPA approves this
alternative monitoring plan for the VCU
pursuant to NSPS subpart J.
Abstract for [0800050]
Q: May British Petroleum Products
North America, Incorporated (British),
Whiting Business Unit in Whiting,
Indiana, use seven hydrogen sulfide
grab samples of loading rack emissions
in lieu of installing a continuous
emission monitoring system as is
required by 40 CFR part 60, subpart J for
a vapor combustion unit (VCU)?
A: No. British has not provided
sufficient information to allow EPA to
make a determination. British needs to
provide additional information
including: (1) An explanation of the
conditions that ensures low amounts of
sulfur in the gas stream at all times; (2)
two weeks of additional daily H2S
monitoring (14 samples); and (3) a
description of how the two weeks of
monitoring results compare to the
typical range of H2S concentration (fuel
quality) expected for the gas stream/
system going to the affected fuel gas
device.
Abstract for [0800051]
Q: Does EPA waive the mercury
testing requirement under the National
Emissions Standards for Mercury at 40
CFR 61.53 for BP Products North
America, Inc. (BP) units in Indiana,
since BP has demonstrated compliance
with the mercury limits under the
National Emission Standards for
Hazardous Air Pollutants for Hazardous
Waste Combustors (HWC MACT)?
A: Yes. EPA approves BP’s request to
use the HWC MACT testing to
demonstrate compliance with the
National Emission Standards for
Mercury since the mercury emissions
are well below the standard in the
regulations.
Abstract for [0800052]
Q: Does EPA approve an alternative
monitoring plan for 40 CFR part 60,
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subpart UUU requirements at the
Criterion Catalysts & Technologies
(Criterion) facility in Michigan City,
Indiana? Criterion requests approval to
continuously monitor the gas flow rate
entering or exiting the wet scrubber in
lieu of continuously monitoring the gas
phase pressure drop across the scrubber.
A: Yes, conditionally. EPA concurs
that the gas phase pressure drop is not
an appropriate continuous monitoring
parameter for a wet scrubber that does
not use a Venturi design for particulate
matter emission control. Pursuant to
NSPS subpart UUU, EPA approves this
alternative monitoring plan subject to
the conditions specified in EPA’s
response letter to Criterion on
September 6, 2007.
Abstract for [0800053]
Q: Does EPA approve an alternative
timeline for well 49 at Davis Junction
Landfill in Davis Junction, Illinois, to
correct an exceedance of the five
percent oxygen concentration standard
under 40 CFR part 60, subpart WWW?
A: Yes. EPA conditionally approves
Davis Junction’s alternative timeline
under NSPS subpart WWW. If Davis
Junction cannot achieve an oxygen
concentration below 5 percent by July 1,
2006, Davis Junction must expand the
gas collection system within 120 days of
the initial measurement of the
exceedance, April 5, 2006.
Abstract for [0800054]
Q: Does EPA approve an alternative
timeline to correct exceedances at the
BFI Waste Systems of North American
Davis Junction Landfill, located in Davis
Junction, Illinois, under 40 CFR part 60,
subpart WWW?
A: Yes. EPA conditionally approves
Davis Junction Landfill’s alternative
timeline under NSPS subpart WWW.
However, if Davis Junction Landfill
cannot achieve an oxygen concentration
below five percent by September 1,
2007, the gas collection system must be
expanded within 120 days of the initial
exceedance.
Abstract for [0800055]
Q: Does EPA approve an alternative
monitoring plan (AMP) for the
ExxonMobil (Exxon) facility in Joliet,
Illinois, under 40 CFR part 60, subpart
J? Exxon requests to continue the
continuous monitoring of the Refinery
Fuel Gas Mix Drum stream, and monitor
an alternate parameter for the disulfide
vent stream.
A: Yes. EPA approves this alternative
monitoring request under NSPS subpart
J. Exxon will continue to continuously
monitor the refinery fuel gas mix drum
stream and will monitor at least three
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times per week the weight percent of the
spent wash for the Caustic Wash Drums
as the alternative parameter in
accordance with the AMP enclose with
EPA’s response.
Abstract for [0800056]
Q: Does EPA find the ALLU unit
associated with the preparatory
processes leading to gypsum stucco
production, at the GP-Gypsum
Corporation (GP) facility in Wheatfield,
Indiana, is not subject to 40 CFR part 60,
subpart OOO?
A: Yes. EPA finds that the ALLU unit
is not subject to NSPS subpart OOO
provisions. The ALLU unit is not part of
the actual nonmetallic mineral
production line and it does not function
as a crusher, screener, or grinder; thus
is not an affected facility subject to
subpart OOO.
Abstract for [0800057]
Q: Does EPA approve the alternative
compliance timeline to correct
exeedances under CFR part 60, subpart
WWW, at the Landcomp Corporation
Landfill (Landcomp), located in Ottawa,
Illinois?
A: No. EPA does not approve of
Landcomp’s request under NSPS
subpart WWW. EPA does grant
alternative compliance timelines to
correct exceedances, but such requests
need to be made within 15 days of the
initial exceedance when the landfill
determines that the exceedance cannot
be corrected.
Abstract for [0800058]
Q: Does EPA approve the alternative
timeline request from American
Disposal Services of Illinois, Inc.’s
Livingston Landfill (Livingston
Landfill), located in Pontiac, Illinois,
under 40 CFR part 60, subpart WWW?
A: Yes. EPA conditionally approves
the alternative timeline under NSPS
subpart WWW from Livingston’s Well
GW51R until December 6, 2007, to
correct the August 8, 2007, positive
pressure. If Livingston Landfill cannot
achieve negative pressure at Well
GW5IR by December 6, 2007, then
Livingston Landfill must expand the gas
collection system within 120 days of the
initial exceedance, August 8, 2007.
Abstract for [0800059]
Q: Does EPA approve the alternative
timeline request from American
Disposal Services of Illinois, Inc.’s
Livingston Landfill (Livingston
Landfill), located in Pontiac, Illinois,
under 40 CFR part 60, subpart WWW?
A: Yes. EPA conditionally approves
the alternative timeline under NSPS
subpart WWW from Livingston’s Well
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GW90 until October 5, 2007, to correct
the July 12, 2007, positive pressure. If
Livingston Landfill cannot achieve
negative pressure at Well GW90 by
October 5, 2007, then Livingston
Landfill must expand the gas collection
system within 120 days of the initial
exceedance, July 12, 2007.
Abstract for [0800060]
Q: Does EPA approve the alternative
timeline request from American
Disposal Services of Illinois, Inc.’s
Livingston Landfill (Livingston
Landfill), located in Pontiac, Illinois,
under 40 CFR part 60, subpart WWW?
A: No. EPA does not approve
Livingston Landfill’s request for an
alternative compliance timeline as of
July 31, 2007, under NSPS subpart
WWW. Although EPA does grant
alternative compliance timelines to
correct exceedances, these requests need
to be made within 15 days of the initial
exceedance when the landfill
determines that the exceedance cannot
be corrected.
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Abstract for [0800061]
Q: Does EPA approve the alternative
timeline request from American
Disposal Services of Illinois, Inc.’s
Livingston Landfill (Livingston
Landfill), located in Pontiac, Illinois,
under 40 CFR part 60, subpart WWW?
A: No. EPA does not approve of
Livingston Landfill’s request for an
alternative compliance timeline of May
30, 2007 under NSPS subpart WWW.
Although EPA does grant alternative
compliance timelines to correct
exceedances, these requests need to be
made within 15 days of the initial
exceedance when the landfill
determines that the exceedance cannot
be corrected.
Abstract for [0800062]
Q: Does EPA approve a request for
alternative temperatures at Waste
Management’s Milam Recycling and
Disposal Facility (Milam) located in East
St. Louis, Illinois, under 40 CFR part 60,
subpart WWW, at wellheads MW48,
MW49, MW50, MW51, MW55, MW56,
and MW57?
A: Yes, on an interim basis. Milam
needs to provide EPA with data that
demonstrate that the increased
temperature at the specific wells will
not cause detrimental results, before it
can provide final approval. EPA will
allow Milam, in the interim, to operate
wells MW48, MW49, MW50, MW51,
MW55, MW56, and MW57 at the
alternative temperature 140 degrees
Fahrenheit and require Milam to report
at least three (3) months worth of data,
demonstrating that the increased
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temperature does not cause subsurface
fires or affect levels of carbon monoxide,
oxygen, or other landfill gas
constituents, including the
methanogenic process.
Abstract for [0800063]
Q: Waste Management’s Milam
Recycling and Disposal Facility (Milam)
located in East St. Louis, Illinois, is
subject to 40 CFR part 60, subpart
WWW (NSPS). Does EPA approve an
alternative temperature of 140 degrees
Fahrenheit at wellheads numbers
MW10, MW11, MW19, MW23, MW24,
MW27, MW29, MW31, MW32, MW38,
MW43, MW47, MW48, MW49, MW50,
MW51, MW55, MW56, MW57, and
MW53?
A: Yes. EPA finds that Milam has
demonstrated that the higher operating
temperatures do not cause subsurface
oxidation. Therefore, EPA approves the
higher operating temperature of 140
degrees Fahrenheit at the wells. Refer
also to Abstract ADI Control No.
0800062.
Abstract for [0800064]
Q: Does EPA approve the alternative
timeline request to correct exceedances
of the five percent oxygen concentration
at the Onyx-Valley View Landfill
(Onyx), which is located in Decatur,
Illinois, under 40 CFR part 60, subpart
WWW? Onyx is specifically requesting
an extension of 30 days to reduce the
oxygen concentration levels below 5
percent.
A: Yes. EPA conditionally approves
Onyx’s alternative timeline of 30 days
under NSPS subpart WWW. If Onyx
cannot achieve an oxygen concentration
below 5 percent within 30 days, Onyx
must expand the gas collection system
within 120 days of the initial
measurement of the exceedance.
Abstract for [0800065]
Q1: Does EPA approve the proposal
from the Veolia Environmental Services
(VES) Orchard Hills Landfill located in
Davis Junction, Illinois, to reduce the
surface monitoring frequency in capped
areas of the landfill to an annual basis,
once three consecutive quarters without
a monitored exceedance of the
operational standard has been
demonstrated in these capped areas,
under 40 CFR part 60, subpart WWW?
A1: No. EPA finds that the reduced
monitoring provision of NSPS does not
apply under NSPS subpart WWW. VESOrchard Hills Landfill must continue to
conduct surface monitoring each quarter
on areas with cover in place.
Q2: Does EPA approve the proposal
from the Veolia Environmental Services
(VES) Orchard Hills Landfill located in
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Davis Junction, Illinois, to widen the
spacing between intervals from 30
meters to 60 meters in areas that have
had or will have synthetic
geomembrane-final cover installed after
three consecutive quarters of surface
emissions monitoring compliance has
been met, under 40 CFR part 60, subpart
WWW?
A2: Yes. EPA conditionally approves
VES-Orchard’s proposal. VES-Orchard’s
can adopt the 60 meters-spacing under
NSPS subpart WWW, but only after data
collected from three quarterly
monitoring events demonstrate that
such widening is appropriate and there
is no exceedances.
Q3: Could EPA clarify for the Veolia
Environmental Services (VES) Orchard
Hills Landfill located in Davis Junction,
Illinois, whether gas collection and
control system connections to leachate
management structures or to interim
landfill gas collectors in areas of the
landfill, which are not yet required to
have controls, are subject to the
monitoring and operating requirements
of 40 CFR part 60, subpart WWW?
A3: No. EPA finds that if the landfill
is not required to install the gas
collection and control system under
NSPS subpart WWW, then it is not
required to monitor or operate that
system.
Abstract for [0800066]
Q: Does EPA approve the alternative
timeline to correct exceedances at the
Allied Waste Industries, inc. Quad
Cities Landfill (Quad Cities) located in
Milan, Illinois, under 40 CFR part 60,
subpart WWW?
A: Yes. EPA approves of Quad Cities’
alternative timeline under NSPS subpart
WWW. However, if Quad Cities cannot
achieve an oxygen concentration below
5 percent by June 30, 2007, Quad Cities
must expand the gas collection system
within 120 days of the initial
exceedance.
Abstract for [0800067]
Q: Quad Cities Landfill (Quad Cities)
located in Milan, Illinois, is subject to
40 CFR part 60, subpart WWW. Does
EPA approve its request to extend the
deadline until December 1, 2006, to
correct an exceedance of the five
percent oxygen concentration standard
at one of its gas collection wells (Well
12)?
A: No. EPA will give Quad Cities until
November 2, 2006, which is 120 days
from the original measured exceedance,
to bring the well into compliance. If
Quad Cities cannot achieve an oxygen
concentration below 5 percent by
November 2, 2006, Quad Cities must
expand the gas collection system within
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120 days of the initial measurement of
the exceedance, July 5, 2006.
Abstract for [0800068]
Q1: Pursuant to 40 CFR 60 subpart
WWW, may BFI Waste Systems of North
America, Inc., Quad Cities Landfill,
Milan, Illinois, waive nitrogen
monitoring at interior wellheads and
monitor only oxygen?
A1: Yes. EPA approves this request
since the NSPS subpart WWW rule
allows for a landfill to monitor either
nitrogen or oxygen.
Q2: Pursuant to 40 CFR 60 subpart
WWW, may BFI Waste Systems of North
America, Inc., Quad Cities Landfill,
Milan, Illinois, meet all operating
conditions 180 days after start-up of
new wells?
A2: No. EPA has reviewed this
request further and still cannot approve
this request.
Q3: Pursuant to 40 CFR 60 subpart
WWW, may BFI Waste Systems of North
America, Inc., Quad Cities Landfill,
Milan, Illinois, treat Quad Cities
Landfill as a separate landfill from
Millennium Waste Landfill to reduce
the frequency of surface scan
requirements?
A3: No. EPA finds that the Quad
Cities Landfill and the Millennium
Waste Landfill are considered one
landfill under the NSPS requirements.
Q4: Pursuant to 40 CFR 60 subpart
WWW, may BFI Waste Systems of North
America, Inc., Quad Cities Landfill,
Milan, Illinois, be exempt from the
monitoring, recordkeeping, and
reporting requirements for treated
landfill gas?
A4: Yes. EPA approved this request in
the BFI Quad Cities treatment of landfill
gas determination letter dated April 5,
2006. As a clarification, EPA approves
the flare as part of the treatment system
when it is combusting treated gas. If the
flare is controlling emissions that are
not treated, then it is subject to the
requirements of 40 CFR 60.752(b)(2)(iii)
(A) and (B).
Q5: Pursuant to 40 CFR 60, subpart
WWW, may BFI Waste Systems of North
America, Inc., Quad Cities Landfill,
Milan, Illinois, consider as approved the
closure report BFI submitted?
A5: No. EPA rejects the report,
because Quad Cities Landfills and
Millennium Landfill are considered one
landfill under NSPS, and EPA requires
the closure report to be submitted when
the landfill, including Quad Cities and
Millennium Landfills, ceases accepting
wastes at the landfill, which has not yet
occurred.
Q6: Pursuant to 40 CFR 60, subpart
WWW, may BFI Waste Systems of North
America, Inc., Quad Cities Landfill,
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Milan, Illinois, be exempt from the
testing requirement under CFR part 60
subpart WWW since the landfill gas is
treated?
A6: Yes. EPA approved this request in
the BFI Quad Cities treatment of landfill
gas determination letter dated April 5,
2006. As a clarification, EPA approves
the flare as part of the treatment system
when it is combusting treated gas. If the
flare is controlling emissions that are
not treated, then it is subject to the
requirements of 40 CFR 60.752(b)(2)(iii)
(A) and (B).
Abstract for [0800069]
Q1: Does EPA consider compression,
de-watering, and filtering the landfill
gas down to at least 10 microns a
treatment under 40 CFR part 60, subpart
WWW, at the BFI Waste Systems of
North America, Incorporated’s Quad
Cities Landfill (BFI) facility located in
Milam, Illinois?
A1: Yes. EPA considers compression,
de-watering, and filtering the landfill
gas down to at least ten microns a
treatment for the purposes of 40 CFR
60.752(b)(2)(iii)(C). This response is
consistent with several previous
determinations made by the Agency and
with the Federal Register Proposed Rule
Amendments dated May 23, 2002.
Q2: How does EPA clarify that once
the landfill gas at the BFI facility is
treated pursuant to 40 CFR
60.752(b)(2)(iii)(C), it is no longer
subject to the testing, monitoring, and
recordkeeping requirements found at
60.752(b)(2)(iii)(B)?
A2: The Federal Register Proposed
Rule Amendments clarify that once the
landfill gas is treated, the facilities that
buy or use the gas have no further
obligations related to the NSPS.
Therefore, EPA finds that BFI would not
be subject to the testing, monitoring,
and recordkeeping requirements located
at 60.752(b)(2)(iii)(B). However,
emissions from any atmospheric vent
from the gas treatment system,
including any compressor, are subject to
the requirements of 40 CFR
60.752(b)(2)(iii)(A) and (B). This does
not include exhaust from an energy
recovery device. This determination is
consistent with previous EPA
determinations. The Federal Register
Proposed Rule Amendments from 2002
are meant to be a clarification of the
existing NSPS, not changes in the rule.
Abstract for [0800070]
Q: Does EPA approve the request for
an alternative timeline to correct
exceedances at the Allied Waste
Industries, Inc. Quad Cities Landfill
(Quad Cities Landfill) located in Milan,
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Illinois, under 40 CFR part 60, subpart
WWW?
A: Yes. EPA conditionally approves
an alternate timeline for Quad Cities
Landfill to correct the oxygen
exceedances at Well 12 but only until
August 29, 2007 (not August 31, 2007 as
Quad Cities Landfill requested). EPA
will only approve an alternate timeline
for correction of oxygen exceedances up
to 120 days of the initial exceedance
which in this case is August 29, 2007.
If Quad Cities Landfill cannot achieve
an oxygen concentration below 5
percent by August 29, 2007, then Quad
Cities Landfill must have the gas
collection system expanded by August
29, 2007, which is 120 days of the initial
exceedance, May 1, 2007.
Abstract for [0800071]
Q: Does EPA approve Natural Gas
Pipeline Company of America’s request
not to monitor the total sulfur content
of the gaseous fuel combusted in the
nine Solar Model Saturn and one Solar
Model Taurus natural gas-fired turbines
at its Compressor Station 113 in
Shorewood, Illinois, as allowed by the
revised Standards of Performance for
Stationary Gas Turbines, 40 CFR part
60, subpart GG?
A: Yes. EPA approves NGPL’s request
not to monitor the total sulfur content
because NGPL provided a Federal
Energy Regulatory Commission (FERC)
tariff sheet for the gaseous fuel,
demonstrating that the ‘‘maximum total
sulfur content of the fuel is less than
20.0 grains/100 scf or less’’ as required
by 40 CFR 60.334(h)(3)(1). The State of
Illinois is the delegated authority and
maintains the right to implement more
stringent requirements than those
outlined above.
Abstract for [0800072]
Q: Does EPA approve the request from
Spoon Ridge Landfill in Fairview,
Illinois, to return to Tier 1 nonmethane
organic compound (NMOC) emission
rate reporting requirements after the
current Tier 2 sampling and NMOC rate
demonstration expires on April 23,
2012, under 40 CFR part 60, subpart
WWW? In lieu of conducting Tier 2
sampling in 2012, Spoon Ridge would
like approval to return to annual NMOC
emission rate reporting in accordance
with 40 CFR 60.752(b)(1)(ii) after 2012.
A: Yes. EPA finds that Tier 2
sampling would be normally required
by April 23, 2012, under NSPS subpart
WWW. If Spoon Ridge does not conduct
this Tier 2 sampling, then 2012
emission would be calculated using Tier
1 analysis.
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Abstract for [0800073]
Q: Does EPA consider that 40 CFR
60.283 applies to total reduced sulfur
(TRS) emissions from digesters’
condensate streams that are discharged
to the waste water treatment system and
released through a sewer stack for
Thilmany, LLC’s Kraft Pulp Mills in
Kaukauna, Wisconsin, under 40 CFR
part 63, subpart BB?
A: No. EPA finds that the emission
limits provided under 40 CFR 60.283 do
not apply to the condensate streams
discharged from Thilmany’s digesters.
The background information documents
(BID) for the Kraft Pulp Mill NSPS
indicates that the intent of subpart BB
was to regulate the TRS emissions in the
non-condensable gases emitted from the
digester systems and not the emissions
caused by the dissolved TRS in the
condensate streams. Furthermore, the
NSPS does not show the sewer stack as
being part of the affected facilities.
Abstract for [0800074]
Q: Does EPA approve the request from
United States Gypsum Company (USG),
located in East Chicago, Indiana, to
waive, under 40 CFR part 60, subpart
OOO, the minimum of 60 dry standard
cubic feet (dscf) of sampling air
collected per run at 40 CFR 60.675(b)(1),
in addition to waiving the two minutes
per point sampling requirement in
Method 5?
A: Yes. EPA conditionally approves
USG to carry out performance testing as
described in the EPA response. This
proposal suggested the sampling volume
be scaled down to 30 dsfc, and that
twelve points in the stack be sampled
for a duration of two and a half minutes
each under 40 CFR part 60, subpart
OOO. USG must operate the shredder
system at its maximum wallboard
processing rate and comply with all
other testing guidelines.
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Abstract for [0800075]
Q: Does EPA find that 40 CFR part 60,
subpart AAa, applies to Alton Steel,
Inc.’s (Alton) Furnace No. 7 (furnace) as
a result of a construction project at the
facility?
A: Yes. EPA finds that it is not
necessary to determine whether the
projects meets one of the modification
exemptions set forth at 40 CFR 60.14(e).
NSPS subpart AAa applies to electric
arc furnaces that are modified after
August 17, 1983, and a modification is
any physical or operational change
which results in an increase in the
emission rate to the atmosphere of any
pollutant to which a standard applies.
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Abstract for [0800076]
Q: Does EPA approve the alternative
monitoring plan requested by CITGO’s
Lemont Refinery for the continuous
opacity monitoring system (COMS) on
the fluid catalytic cracking unit (FCCU),
under 40 CFR part 60, subpart J? CITGO
entered into a Consent Decree in
January 2005, which required the
Lemont Refinery to install a wet gas
scrubber (WGS) on the FCCU unit.
CITGO maintains that the moisture in
the exhaust from the WGS will interfere
with the ability of the COMBS to take
accurate readings.
A: Yes. EPA approves an alternative
monitoring plan for CITGO pursuant to
40 CFR 60.13(i)(1). The specific points
of the alternative monitoring plan are
specified in EPA’s response to CITGO
on July 23, 2007.
Abstract for [0800077]
Q: Does EPA approve the alternative
timeline to correct exceedances at the
Davis, Junction Landfill (Davis
Junction), located in Davis Junction,
Illinois, under 40 CFR part 60, subpart
WWW?
A: Yes. EPA approves Davis
Junction’s alternative timeline under
NSPS subpart WWW. If Davis Junction
cannot achieve an oxygen concentration
below five percent by June 1, 2007, the
facility must expand the gas collection
system within 120 days of the initial
exceedance.
Abstract for [0800078]
Q: Does EPA approve the alternative
timeline to correct exceedances at the
Davis, Junction Landfill (Davis
Junction), located in Davis Junction,
Illinois, under 40 CFR part 60, subpart
WWW?
A: Yes. EPA conditionally approves
Davis Junction’s alternative timeline
under NSPS subpart WWW. If Davis
Junction cannot achieve an oxygen
concentration below five percent by
June 1, 2007, the facility must expand
the gas collection system within 120
days of the initial exceedance.
Abstract for [0800079]
Q: Does EPA consider the landfill gas
at the Devonshire Power partners, LLC
(Devonshire) Landfill, located in Dolton,
Illinois, subject to the New Source
Performance Standards (NSPS) and
National Emission Standard for
Hazardous Air Pollutants (NESHAP)
requirements once treated per 40 CFR
60.752(b)(2)(iii)(c)?
A: No. EPA finds that once landfill
gas is treated pursuant to 40 CFR
60.752(b)(2)(iii)(c), that the gas is no
longer subject to the monitoring and
recordkeeping requirements found at 40
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Sfmt 4703
80405
CFR 60.756(b) and 60.758(b) and (c).
The determination letter includes
further compliance information.
Abstract for [0800080]
Q: Does EPA find it acceptable to
inject an excess of hydrogen peroxide
(H2O2) into the wastewater stream as a
means to control the hydrogen sulfide
(H2S) emissions, instead of using a
continuous monitoring system (CMS) on
the infrequently operated North
Benzene Removal Unit (NBRU), at the
ExxonMobil Joliet Refinery, in Joliet,
Illinois, under 40 CFR part 60, subpart
J?
A: Yes. EPA finds that the hydrogen
peroxide injection and residual
hydrogen peroxide meter are a sufficient
replacement of the H2S CMS. However,
EPA is not assured that 5 ppm H2O2 is
an adequate limit to ensure compliance.
EPA requires a preliminary value of at
least 10 parts per million. Once
ExxonMobil has submitted sufficient
data to show that this limit can be
lower, EPA will consider reducing the
limit. EPA’s May 2, 2007 response letter
contains further details.
Abstract for [0800081]
Q: Does EPA approve the alternative
monitoring plan for propane vapor from
a vent gas absorber (VGA), requested by
the ExxonMobil Joliet Refinery, located
in Joliet, Illinois, under 40 CFR part 60,
subpart J? ExxonMobil’s proposal is to
remove the car seal and allow vent gas
from the VGA to be routed either to the
alkylation unit’s isostripper reboiler
heater, or to a flare.
A: Yes. EPA conditionally approves
the alternative monitoring plan under
NSPS subpart J. However, the Joliet
facility is required to conduct a
monitoring schedule per the conditions
detailed in EPA’s April 26, 2008
response letter.
Abstract for [0800082]
Q: Does EPA approve the alternative
monitoring plan (AMP) submitted by
ExxonMobil’s Joliet Refinery, located in
Joliet, Illinois, for demonstrating
compliance with the opacity limit under
40 CFR part 60, subpart J? The Joliet
Refinery currently operates a
continuous monitoring system (COMS)
to demonstrate compliance.
A: Conditional. EPA approves
alternative monitoring pursuant to 40
CFR part NSPS, subpart J, given five
conditions are met, as outlined in the
Agency’s response to ExxonMobil on
February 5, 2007.
Abstract for [0800083]
Q: Does EPA find that 40 CFR part 60,
subpart DD, applies to a grain terminal
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elevator when co-located with other
facilities, as described per the request of
the Illinois Environmental Protection
Agency?
A: Yes. EPA finds that the
applicability of NSPS subpart DD to a
grain terminal elevator would not be
impacted by entering into a contractual
agreement with an ethanol plant. In
respect to NSPS subpart DD, EPA
outlined several issues regarding
ownership and facilities with multiple
products, as described in the EPA
response letter of April 12, 2007.
Abstract for [0800084]
Q: Does EPA approve the request from
the United States Gypsum Company
(USG), for an alternative method for
fulfilling the testing requirements at 40
CFR part 60, subpart OOO? Specifically,
USG requests that Method 9 visible
emission readings be utilized as an
alternative method of fulfilling the test
methods and procedures for
determining compliance with the
particulate matter standards.
A: No. EPA denies USG’s request
under NSPS subpart OOO. EPA will
allow USG to reduce the time of each of
the three test runs to thirty minutes as
an alternative performance testing
arrangement to fulfill the testing
requirements of NSPS subpart OOO.
USG must operate the shredder system
at its maximum wallboard processing
rate and comply with all other testing
guidelines required.
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Abstract for [0800085]
Q: Does EPA approve the alternative
timeline request from the Valley View
Landfill (Valley View), located in
Decatur, Illinois, to correct an
exceedance under 40 CFR part 60,
subpart WWW?
A: Yes. EPA conditionally approves
Valley View’s alternative timeline under
NSPS subpart WWW. If Valley cannot
achieve an oxygen concentration below
five percent by October 7, 2006, Valley
View must expand the gas collection
system within 120 days of the initial
measurement of the exceedance.
Abstract for [0800086]
Q: Does EPA approve the change in
standard operating procedures for Wells
GEW–14, GEW–16, and GEW–28 at the
Veolia Orchard Hills Landfill (VOHL),
located in Davis Junction, Illinois, under
40 CFR part 60, subpart WWW?
Specifically, VOHL requests a change
involving oxygen concentration
monitoring.
A: Yes. EPA conditionally approves,
in part, VOHL’s request to change
standard operating procedures for the
specified Wells under NSPS subpart 60.
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Jkt 217001
VOHL must continue to monitor wells
for pressure, oxygen, and temperature,
as well as surface monitoring for
methane. VOHL must perform all
necessary actions to bring oxygen
concentrations below the five percent
threshold and report any exceedances.
Specific changes to the standard
operating procedures are listed in EPA’s
response letter dated March 28, 2007.
Abstract for [0800087]
Q: Is a process that will collect
hydrogen sulfide and other sulfur
compounds and further process them to
produce sulfuric acid at a synthetic
natural gas plant at Power Holdings,
LLC, in Illinois, subject to the New
Source Performance Standards for
Sulfuric Acid Plants at 40 CFR part 60,
subpart H?
A: Yes. EPA finds that NSPS subpart
H applies to Power Holdings because
the plant will collect hydrogen sulfide
and other sulfur compounds and further
process them to produce sulfuric acid.
Hydrogen sulfide will be burned.
Furthermore, the plant would not be
exempt from the rule because it is not
a metallurgical plant, a chamber process
plant, or an acid concentrator.
Abstract for [M080037]
Q: Request for guidance on
implementation and compliance
monitoring of the capture, collection
and ventilation requirements in the
Secondary Aluminum MACT, subpart
RRR.
A: The Secondary Aluminum MACT
adopts by reference Chapters 3 and 5 of
the Industrial Ventilation: A Manual of
Recommended Practice, 23rd edition,
published by the American Conference
of Governmental Industrial Hygienists
(ACGIH). As required by 40 CFR
63.1506(c) of subpart RRR, owners or
operators of affected sources or
emissions units with add-on air
pollution control devices must: Design
and install a system for the capture and
collection of emissions to meet the
engineering standards for minimum
exhaust rates as published by the
American Conference of Governmental
Industrial Hygienists in chapters 3 and
5 of ‘‘Industrial Ventilation: A Manual
of Recommended Practice.’’
Abstract for [M080036]
Q: How can an owner or operator of
a secondary aluminum production
facility know that the scrap they are
processing is ‘‘entirely free of paints,
coatings, and lubricants’’?
A: Knowledge of whether the scrap
material being processed is ‘‘entirely
free of paints, coatings, and lubricants’’
can be gained through two methods.
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Fmt 4703
Sfmt 4703
One method would be to maintain
direct control of the scrap material being
processed by processing scrap generated
within the facility or from other
facilities within the same company that
the owner or operator knows has not
been subjected to paints, coatings and
lubricants or where they know paints,
coatings and lubricants have been
removed consistent with the definition
of ‘‘Clean charge.’’ Similarly, the owner
or operator also may process scrap from
outside entities where they are familiar
with the history of the scrap and,
therefore, know that the scrap meets the
definition of ‘‘Clean charge.’’
Abstract for [0800088]
Q1. Is the addition of three vent
streams from the Delayed Coker Unit
(DCU) to the common flare header
connecting three flares at the Shell’s
Puget Sound Refinery (PSR) facility
(DCU Project) that occurred in 1983
considered a modification of the flare
under the New Source Performance
Standards (NSPS) for Petroleum
Refineries, subpart J?
A1. Yes. EPA has determined that the
DCU Project resulted in a modification
of the PSR flares triggering NSPS
subpart J applicability. The physical
change that was made upstream of the
flares at a refinery process unit occurred
after the effective date of the rule and it
resulted in an operational change to the
PSR flares since combusting gas streams
not previously combusted in the flare is
a change in how the flare operates. The
operational change to the PSR flares
resulted in an increase in the sulfur
dioxide emissions rate to the
atmosphere such that they were
modified under the NSPS.
Q2. Is the redesign and replacement of
the flare tip, a physical change to the
PSR East Flare facility made in 1990,
considered a modification of the flare
under the NSPS subpart J?
A2. EPA agrees that if in fact the
replacement of the PSR flare tip resulted
in a decrease of its maximum capacity,
the redesigned flare was not modified
under the NSPS provisions and is not
subject to NSPS subpart J. The change
would decrease the kilograms per hour
of hydrogen sulfide routed to the flare,
resulting in an emissions decrease of
sulfur dioxide emissions to the
atmosphere.
Abstract for [0800089]
Q: Are the dryers at a bark burner
system at a Louisiana-Pacific OSB
facility in Thomasville, Alabama,
‘‘process heaters’’ and thereby excluded
from 40 CFR part 60, subpart Db?
A: No. The definition of steam
generating unit under NSPS subpart Db
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excludes ‘‘process heaters,’’ which are
defined as devices used primarily to
heat a material to initiate or promote a
chemical reaction. The primary purpose
of heating wood flakes in the dryers is
to dry them, rather than to invoke a
chemical reaction either within the
dryers or downstream of the dryers.
Therefore, the dryers do not qualify for
the process heater exclusion.
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Abstract for [0800090]
Q1: Does NSPS subpart J apply to the
proposed Hyperion Energy Center (HEC)
near Elk Point, South Dakota?
A1: No. Subpart J applies to various
affected facilities at petroleum refineries
based on the date the affected facility
commenced construction,
reconstruction, or modification. Since
the Hyperion Energy Center has not yet
begun construction it is not subject to
Subpart J. To be subject to subpart J,
HEC’s Claus sulfur recovery plant and
fuel gas combustion devices would have
had to begin construction on or before
May 14, 2007, except for flares, which
would have had to begin construction
on or before June 24, 2008.
Q2: Do the synthetic gas and pressure
swing adsorption (PSA) tail gas to be
produced at the integrated gasification
combined cycle power plant gasification
block at the proposed Hyperion Energy
Center near Elk Point, South Dakota,
constitute ‘‘fuel gas’’ under 40 CFR part
60, subpart Ja?
A2: Yes. Because the synthetic gas
and PSA tail gas will be generated at a
petroleum refinery and combusted and
meet the definition of ‘‘fuel gas’’ in 40
CFR 60.101a, therefore these are subject
to NSPS subpart Ja. This definition is
not restricted to gas produced by a
refinery process unit, but even if it were,
the gasification block will be a refinery
process unit, because it is a segment of
a refinery in which gasification, a
specific processing operation, will be
conducted.
Abstract for [Z080005]
Q: Is a proposed integrated
gasification combined cycle (IGCC)
power plant at the Hyperion Energy
Center near Elk Point, South Dakota,
subject to 40 CFR part 63, subpart CC?
A: Yes. Subpart CC applies to the
IGCC system. The IGCC system is a
‘‘petroleum refining process unit’’
because it will be located at an
establishment primarily engaged in
petroleum refining and because it
produces hydrogen. Additionally, the
IGCC system will be located at a plant
site where: (1) The plant site is a major
source of hazardous air pollutants
(HAPs), and (2) the IGCC system emits
or has equipment containing or
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17:41 Dec 30, 2008
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contacting one or more of the HAPs
listed in Table 1 of Subpart CC.
Dated: December 23, 2008.
Lisa Lund,
Director, Office of Compliance.
[FR Doc. E8–31117 Filed 12–30–08; 8:45 am]
BILLING CODE 6560–50–P
FEDERAL COMMUNICATIONS
COMMISSION
Notice of Public Information
Collection(s) Being Submitted for
Review to the Office of Management
and Budget
December 19, 2008.
SUMMARY: The Federal Communications
Commission, as part of its continuing
effort to reduce paperwork burden
invites the general public and other
Federal agencies to take this
opportunity to comment on the
following information collection(s), as
required by the Paperwork Reduction
Act (PRA) of 1995, 44 U.S.C. 3501–3520.
An agency may not conduct or sponsor
a collection of information unless it
displays a currently valid control
number. No person shall be subject to
any penalty for failing to comply with
a collection of information subject to the
Paperwork Reduction Act (PRA) that
does not display a valid control number.
Comments are requested concerning (a)
whether the proposed collection of
information is necessary for the proper
performance of the functions of the
Commission, including whether the
information shall have practical utility;
(b) the accuracy of the Commission’s
burden estimate; (c) ways to enhance
the quality, utility, and clarity of the
information collected; and (d) ways to
minimize the burden of the collection of
information on the respondents,
including the use of automated
collection techniques or other forms of
information technology.
DATES: Written Paperwork Reduction
Act (PRA) comments should be
submitted on or before March 2, 2009.
If you anticipate that you will be
submitting PRA comments, but find it
difficult to do so within the period of
time allowed by this notice, you should
advise the FCC contact listed below as
soon as possible.
ADDRESSES: Direct all PRA comments to
Nicholas A. Fraser, Office of
Management and Budget, (202) 395–
5887, or via fax at 202–395–5167 or via
Internet at
Nicholas_A._Fraser@omb.eop.gov and
to Judith-B.Herman@fcc.gov, Federal
Communications Commission, or an
e-mail to PRA@fcc.gov. To view a copy
PO 00000
Frm 00047
Fmt 4703
Sfmt 4703
80407
of this information collection request
(ICR) submitted to OMB: (1) Go to the
Web page https://www.reginfo.gov/
public/do/PRAMain, (2) look for the
section of the Web page called
‘‘Currently Under Review’’, (3) click on
the downward-pointing arrow in the
‘‘Select Agency’’ box below the
‘‘Currently Under Review’’ heading, (4)
select ‘‘Federal Communications
Commission’’ from the list of agencies
presented in the ‘‘Select Agency’’ box,
(5) click the ‘‘Submit’’ button to the
right of the ‘‘Select Agency’’ box, and (6)
when the list of FCC ICRs currently
under review appears, look for the title
of this ICR (or its OMB Control Number,
if there is one) and then click on the ICR
Reference Number to view detailed
information about this ICR.
FOR FURTHER INFORMATION CONTACT: For
additional information, contact Judith B.
Herman at 202–418–0214 or via the
Internet at Judith-B.Herman@fcc.gov.
SUPPLEMENTARY INFORMATION:
OMB Control Number: 3060–0848.
Title: Deployment of Wireline
Services Offering Advanced
Telecommunications Capability, CC
Docket No. 98–147.
Form No.: N/A.
Type of Review: Revision of a
currently approved collection.
Respondents: Business or other forprofit.
Number of Respondents: 1,400
respondents; 17,340 responses.
Estimated Time per Response: .50–26
hours.
Frequency of Response: On occasion
reporting requirement and third party
disclosure requirement.
Obligation To Respond: Required to
obtain or retain benefits. Statutory
authority for these information
collections are contained in 47 U.S.C.
Sections 151–154, 201–203, 251–254,
256 and 303(r) of the Communications
Act of 1934, as amended.
Total Annual Burden: 61,490 hours.
Total Annual Cost: N/A.
Privacy Act Impact Assessment: N/A.
Nature and Extent of Confidentiality:
The Commission is not requesting
respondents to submit confidential
information to the Commission. If the
Commission requests respondents
submit information which respondents
believe is confidential, respondents may
request confidential treatment of such
information under 47 CFR 0.459 of the
Commission’s rules.
Needs and Uses: The Commission
will submit this information collection
to the Office of Management and Budget
(OMB) after this 60 day comment period
in order to obtain the full three year
clearance from them. The Commission
E:\FR\FM\31DEN1.SGM
31DEN1
Agencies
[Federal Register Volume 73, Number 251 (Wednesday, December 31, 2008)]
[Notices]
[Pages 80392-80407]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-31117]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
[FRL-8759-4]
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 control number, date, author, subpart, or subject search.
For questions about the ADI or this notice, contact Maria Malave at EPA
by phone at: (202) 564-7027, or by e-mail at: malave.maria@epa.gov. For
technical questions about the individual applicability determinations
or monitoring decisions, refer to the contact person identified in the
individual documents, or in the absence of a contact person, refer to
the author of the document.
SUPPLEMENTARY INFORMATION: Background: The General Provisions to the
NSPS in 40 Code of Federal Regulations (CFR) part 60 and the NESHAP in
40 CFR part 61 provide that a source owner or operator may request a
determination of whether certain intended actions constitute the
commencement of construction, reconstruction, or modification. EPA's
written responses to these inquiries are commonly referred to as
applicability determinations. See 40 CFR 60.5 and 61.06. Although the
part 63 NESHAP and section 111(d) of the Clean Air Act regulations
contain no specific
[[Page 80393]]
regulatory provision that sources may request applicability
determinations, EPA does respond to written inquiries regarding
applicability for the part 63 and section 111(d) programs. The NSPS and
NESHAP also allow sources to seek permission to use monitoring or
recordkeeping that are different from the promulgated requirements. See
40 CFR 60.13(i), 61.14(g), 63.8(b)(1), 63.8(f), and 63.10(f). EPA's
written responses to these inquiries are commonly referred to as
alternative monitoring decisions. Furthermore, EPA responds to written
inquiries about the broad range of NSPS and NESHAP regulatory
requirements as they pertain to a whole source category. These
inquiries may pertain, for example, to the type of sources to which the
regulation applies, or to the testing, monitoring, recordkeeping or
reporting requirements contained in the regulation. EPA's written
responses to these inquiries are commonly referred to as regulatory
interpretations.
EPA currently compiles EPA-issued NSPS and NESHAP applicability
determinations, alternative monitoring decisions, and regulatory
interpretations, and posts them on the ADI on a quarterly basis. In
addition, the ADI contains EPA-issued responses to requests pursuant to
the stratospheric ozone regulations, contained in 40 CFR part 82. The
ADI is an electronic index on the Internet with over one thousand EPA
letters and memoranda pertaining to the applicability, monitoring,
recordkeeping, and reporting requirements of the NSPS 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 107 such documents added to
the ADI on December 12, 2008 and December 23, 2008. 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.
Summary of Headers and Abstracts
The following table identifies the database control number for each
document posted on the ADI database system on December 12, 2008 and
December 23, 2008; the applicable category; the subpart(s) of 40 CFR
part 60, 61, or 63 (as applicable) covered by the document; and the
title of the document, which provides a brief description of the
subject matter.
We have also included an abstract of each document identified with
its control number after the table. These abstracts are provided solely
to alert the public to possible items of interest and are not intended
as substitutes for the full text of the documents. This notice does not
change the status of any document with respect to whether it is ``of
nationwide scope or effect'' for purposes of section 307(b)(1) of the
Clean Air Act. For example, this notice does not make an applicability
determination for a particular source into a nationwide rule. Neither
does it purport to make any document that was previously non-binding
into a binding document.
ADI Determinations Uploaded on December 12, 2008
------------------------------------------------------------------------
Control number Category Subpart Title
------------------------------------------------------------------------
A080001.............. NSPS........... J......... Alternative
Monitoring Plan for
Refinery Fuel Gas.
M080005.............. MACT........... EEEEE..... Force Majeure Events
Delaying Initial
Performance Testing
for an Iron and
Steel Foundry.
M080006.............. MACT........... EEEEE..... Disapproval of
Alternative Stack
Testing Request.
M080007.............. MACT........... DDDDD..... Request to
Substitute Flue Gas
Temperature
Monitoring for
Pressure Drop
Monitoring.
M080008.............. MACT........... YY........ Control Requirement
for Plant Exhaust
from Primary Bag
Filter Vents when
Routed and not
Routed to a
Cogeneration Unit.
M080009.............. MACT........... IIIII..... Continuous
Compliance
Requirements for
Mercury Recovery
Units.
M080010.............. MACT........... EEEEE..... Storage and Transfer
of Toluene Used as
Fuel.
M080011.............. MACT........... FFFF...... Multiple Standard
Batches to Define a
Process within a
Single MCPU.
M080012.............. MACT........... GGG, FFFF. MON Rule and
Pharmaceuticals
NESHAP for
Glucosamine
Hydrochloride.
M080013.............. MACT........... FFFF...... Manufacture of Poly
Methyl Methacrylate
(PMMA) Acrylic
Sheet.
M080014.............. MACT........... MMM, SS... Initial Compliance
Demonstration for
Thermal Treatment
Units.
M080016.............. MACT........... GGG....... Process Condensers
and 20 ppmv Limit
without Calculating
Uncontrolled
Emissions.
M080017.............. MACT........... MMM, SS... Use of Previously
Conducted
Performance Tests
for Initial
Compliance
Demonstration.
M080018.............. MACT........... N......... Alternative Testing,
Monitoring, and
Work Practice
Standards.
M080019.............. MACT........... RRR....... Request for Waiver
of Performance
Tests for Low-speed
Aluminum Scrap
Shredders.
M080020.............. MACT........... UUUU...... Request for
Alternative
Monitoring Plan
Following
Replacement of GC/
PID Instrument.
Z080003.............. NESHAP......... F......... Alternative
Monitoring Plan
Modification.
800017............... NSPS........... Db........ Alternative
Monitoring
Procedure for
Opacity.
800018............... NSPS........... WWW....... Alternative
Monitoring
Requests.
800019............... NSPS........... WWW....... Alternative
Monitoring
Requests.
800020............... NSPS........... WWW....... Alternative
Monitoring
Requests.
800021............... NSPS........... J, Ja..... Gap in Continuous
Program of
Construction for
Process Heater.
800022............... NSPS........... WWW....... Request for Higher
Operating
Temperature at
Landfill Wellhead.
800023............... NSPS........... WWW....... Request for Higher
Operating
Temperature at
Landfill Wellhead.
800024............... NSPS........... WWW....... Alternative
Compliance Timeline
for Landfill.
800025............... NSPS........... CC........ Bridgewall Optical
Temperature (BWOT)
Alternative
Monitoring
Proposal.
800026............... NSPS........... WWW....... Alternative
Compliance Timeline
for Landfill Well.
800027............... NSPS........... Db, Dc.... Indirect-Fired
Dryers used in the
Ethanol Industry.
800028............... NSPS........... UUU....... Synthetic Alumina
Applicability
Determination.
800029............... NSPS........... D......... Continuous
Particulate
Emission Monitoring
System.
800030............... NSPS........... D......... Continuous
Particulate
Emission Monitoring
System.
800031............... NSPS........... KKKK...... Reconstruction of a
Stationary
Combustion Turbine.
800032............... NSPS........... VV, VVa... Alternative
Monitoring
Procedure for Leak
Detection.
800033............... NSPS........... J......... Revised Alternative
Monitoring Plan
Conditions for
Hydrogen Sulfide.
[[Page 80394]]
800034............... NSPS........... Dc........ Boiler Derate
Proposal.
800035............... NSPS........... WWW....... Alternative
Compliance Timeline
for Landfill Well.
800036............... NSPS........... KKK....... Applicability to
Expansion Project
at Propane
Refrigeration
Plant.
800037............... NSPS........... UUU....... Alternative
Monitoring for
Calciner.
800038............... NSPS........... WWW....... Alternative
Compliance Timeline
for Leachate
Recirculation Line.
800039............... NSPS........... WWW....... Alternative Timeline
to Correct Positive
Pressure at
Landfill Wells.
800040............... NSPS........... WWW....... Alternative
Standards/
Procedures for
Oxygen/Pressure.
800041............... NSPS........... Kb........ Process Tanks
Defined.
800042............... NSPS........... Kb........ Request for
Reconsideration of
Gasoline Storage
Vessel Decision.
800043............... NSPS........... GG, KKKK.. Original owner/
operator of Gas
Turbine.
800044............... NSPS........... Da........ Modification to
Increase Feed Rate
with Bottleneck.
800045............... NSPS........... Da........ Modification to
Increase Feed Rate
with Bottleneck.
M080021.............. MACT........... RRR....... Applicability to
Aluminum Shredder/
Baler.
M080022.............. MACT........... NNNNN..... Alternative
Monitoring for
Water Scrubber/Mist
Eliminator.
M080023.............. MACT........... RRR....... Thermal Chip Dryer
Operation Prior to
Performance
Testing.
M080024.............. MACT........... KKKK...... Applicability
determination for
Metal Can Surface
Coating NESHAP.
M080025.............. MACT........... G......... Alternative
Monitoring
Parameters for HON
Carbon Adsorber
System.
M080026.............. MACT........... G......... Alternative
Monitoring
Parameters for HON
Carbon Adsorber
System.
M080027.............. MACT........... RRR....... Dioxin/Furan Stack
Test Waiver
Request.
M080028.............. MACT........... RRR....... Dioxin/Furan State
Test Waiver
Request, OM & M
Plan Deficiencies,
and Lime Injection.
M080029.............. MACT........... CC, R..... Alternate Monitoring
Parameter for
Assist Gas in
Flare.
M080031.............. MACT........... DDDDD..... Definition of
Process Heater.
M080034.............. MACT........... FFFFF..... Stack Test Waiver
Request.
M080035.............. MACT........... JJJJ...... Compliance
Demonstration for
Paper and Other Web
Coating.
Z080004.............. NESHAP......... E......... Applicability for
Sludge Dryer.
800046............... NSPS........... DD........ Applicability and
Alternative Control
Conditions for
Malting Facility.
800047............... NSPS........... WWW....... Treated Landfill Gas
Exemption.
800048............... NSPS........... J......... Alternative
Monitoring Plan at
Petroleum Refinery.
800049............... NSPS........... J......... Alternative
Monitoring for
Petroleum Refinery
Vapor Combustion
Unit.
800050............... NSPS........... J......... Alternative
Monitoring for
Petroleum Refinery
Vapor Combustion
Unit.
800051............... NESHAP......... E......... Waiver of Mercury
Emissions Testing
for Refinery.
800052............... NSPS........... UUU....... Alternative
Monitoring for Wet
Scrubber.
800053............... NSPS........... WWW....... Alternative Timeline
to Correct
Exceedances at
Landfill Well.
800054............... NSPS........... WWW....... Alternative Timeline
to Correct
Exceedances at
Landfill Well.
800055............... NSPS........... J......... Alternative
Monitoring for
Vapors from
Disulfide Separator
Venting.
800056............... NSPS........... OOO....... Preparatory
Processes for
Gypsum Stucco
Production.
800057............... NSPS........... WWW....... Alternative Timeline
to Correct
Exceedances at
Landfill Well.
800058............... NSPS........... WWW....... Alternative Timeline
to Correct
Exceedances at
Landfill Well.
800059............... NSPS........... WWW....... Alternative Timeline
to Correct
Exceedances at
Landfill Well.
800060............... NSPS........... WWW....... Alternative Timeline
to Correct
Exceedances at
Landfill Wells.
800061............... NSPS........... WWW....... Alternative Timeline
to Correct
Exceedances at
Landfill Well.
800062............... NSPS........... WWW....... Alternative
Temperature at
Recycling and
Disposal Facility.
800063............... NSPS........... WWW....... Alternative
Temperature at
Recycling and
Disposal Facility.
800064............... NSPS........... WWW....... Alternative Timeline
to Correct
Exceedances at
Landfill Well.
800065............... NSPS........... WWW....... Alternative
Monitoring
Procedures at a
Landfill.
800066............... NSPS........... WWW....... Alternative Timeline
to Correct
Exceedance at
Landfill Well.
800067............... NSPS........... WWW....... Alternative Timeline
to Correct
Exceedance at
Landfill Well.
800068............... NSPS........... WWW....... Alternative
Monitoring,
Testing, and Other
Requirements for a
Landfill.
800069............... NSPS........... WWW....... Treated Landfill Gas
Exemption.
800070............... NSPS........... WWW....... Alternative Timeline
to Correct
Exceedance at
Landfill Well.
800071............... NSPS........... GG........ Revision of Custom
Fuel Monitoring
Schedule.
800072............... NSPS........... WWW....... Emissions Rate
Reporting
Requirements at
Landfill.
800073............... NSPS........... BB........ Applicability
Determination for
Kraft Pulp Mill TRS
Emissions.
800074............... NSPS........... OOO....... Performance Testing
Requirement
Condition D.4.6.
800075............... NSPS........... AAa....... Installation of a
Capacitor/Reactor
at an Electric Arc
Furnace.
800076............... NSPS........... J......... Alternative
Monitoring for
Opacity Due to Wet
Gas Scrubber.
800077............... NSPS........... WWW....... Alternative Timeline
to Correct
Exceedance at a
Landfill Well.
800078............... NSPS........... WWW....... Alternative Timeline
to Correct
Exceedance at a
Landfill Well.
800079............... NSPS........... AAAA, WWW. Landfill Gas
Treatment
Exemption.
800080............... NSPS........... J......... Alternative
Monitoring for
Thermal Vapor
Incinerator.
800081............... NSPS........... J......... Alternative
Monitoring Plan for
Propane Vapor from
a Vent Gas
Absorber.
800082............... NSPS........... J......... Alternative
Monitoring Request
for FCCU COMS at a
Refinery.
800083............... NSPS........... DD........ Applicability for Co-
Located Grain
Elevators.
800084............... NSPS........... OOO....... Alternative Testing
Method Request for
Wallboard Shredder.
800085............... NSPS........... WWW....... Alternative Timeline
to Correct
Exceedance at a
Landfill Well.
800086............... NSPS........... WWW....... Change to Standard
Operating Procedure
at a Landfill.
800087............... NSPS........... H......... Applicability for
Sulfuric Acid
Plants with
Hydrogen Sulfide
Burning Processes.
M080037.............. MACT........... RRR....... Compliance with
ACGIH Ventilation
Manual.
M080036.............. MACT........... RRR....... Clean Charge
Defined.
0800088.............. NSPS........... J......... Applicability to a
Refinery Flare.
[[Page 80395]]
ADI Determinations Uploaded on December 23, 2008
������������������������������������������������������������������������
0800089.............. NSPS........... Db........ Dryers at OSB Bark
Burner System.
0800090.............. NSPS........... J, Ja..... Integrated
Gasification
Combined Cycle
Power Plant.
Z080005.............. NESHAP......... CC........ Integrated
Gasification
Combined Cycle
Power Plant.
------------------------------------------------------------------------
Abstracts
Abstract for [A080001]
Q: Does EPA allow ConocoPhillips' Wood River Refinery in Roxana,
Illinois, to monitor the liquid benzene at the finished product tanks
under 40 CFR part 60, subpart J, in lieu of continuously monitoring the
sulfur dioxide concentration of the displaced barge vapors from benzene
loading? These displaced barge vapors are directed to the Marine Vapor
Control system thermal oxidizer.
A: Yes. EPA finds that the proposed alternative monitoring proposal
from ConocoPhillips meets the requirements of EPA's guidance entitled
``Alternative Monitoring Plan for NSPS subpart J Refinery Fuel Gas.''
The displaced benzene vapors from the benzene loading are inherently
low in sulfur content.
Abstract for [M080005]
Q: Does EPA consider, as force majeure, certain furnace
malfunctions and labor strikes that prevented stack tests from being
conducted before the compliance deadline under 40 CFR part 63, subpart
EEEEE, at the Indianapolis Casting facility in Indianapolis, Indiana?
A: Yes. EPA finds that the certain events, such as furnace
malfunctions and labor strikes, as described in EPA's response to
Indianapolis Casting, can be considered as force majeure under MACT
subpart A. The furnace malfunctions were safety related and required
extended furnace shut downs for repair, and labor actions are beyond
the control of the company.
Abstract for [M080006]
Q: Does EPA accept stack test results performed before the
compliance deadline of 40 CFR part 63, subpart EEEEE, as the required
initial compliance demonstration at the Indianapolis Casting facility
in Indianapolis, Indiana?
A: Yes. EPA accepts stack test results before the compliance
deadline under MACT subpart EEEEE as the initial compliance
demonstration only if the production rates achieved during the April
2005 tests are representative of the highest production rates currently
achievable, and the gas sample volume collected meets or exceeds 60 dry
standard cubic feet for each sampling run as specifically required
under 40 CFR 63.7732(b)(2).
Abstract for [M080007]
Q: Does EPA allow S.D. Warren to monitor the flue gas temperature
of the wet scrubber outlet in lieu of monitoring the pressure drop
across the wet scrubber under 40 CFR part 63, subpart DDDDD? The S.D.
Warren Company/SAPPI Fine Paper of North America's Skowhegan, Maine,
pulp mill has a large multi-fuel boiler with an associated wet scrubber
that does not experience a significant pressure drop because it is an
open vessel.
A: Yes. EPA finds this acceptable under MACT subpart DDDDD. A
temperature drop in the range of 250 degrees Fahrenheit at the scrubber
outlet will indicate that the flue gases are coming into contact with
the scrubber water in order to control particulate matter emissions. A
continuous monitoring system that can be used to determine and record
the flue gas temperature of the boiler wet scrubber outlet at least
once every successive 15-minute period should be installed, calibrated,
maintained, and operated.
Abstract for [M080008]
Q: What are the applicability and control requirements under 40 CFR
part 63, subpart YY, for the plant exhaust from the primary bag filter
vents for Units 1, 2, and 3 at the Sid Richardson Big Springs facility
in Howard County, Texas, which are primarily routed to a cogeneration
unit but also can be routed away from the facility's cogeneration unit
to a flare?
A: The facility would be subject to different requirements under
MACT subpart YY depending upon the use of the exhaust gas. When the
facility routes the exhaust gas to the cogeneration unit, no control
requirements would apply. During the times the facility bypasses the
cogeneration system to the flare, the plant exhaust from the primary
bag filter vents for Units 1, 2, and 3 must meet the requirements under
MACT subpart YY for process vents, unless there is a startup, shutdown,
or malfunction (SSM). When the plant exhaust from the primary bag
filter vents for Units 1, 2, and 3 bypasses the cogeneration unit
during SSM, the facility must follow its SSM plan.
Abstract for [M080009]
Q: Does 40 CFR part 63, subpart IIIII require a daily average or an
hourly average to determine continuous compliance with the emissions
standard for mercury recovery units under Section 63.8190(a)(3)?
A: When determining continuous compliance with the emissions
standard for mercury recovery units under 40 CFR 63.8190(a)(3), a
facility should calculate a daily average mercury concentration, using
Equation 2 at 40 CFR 63.8240(a).
Abstract for [M080010]
Q: Does the exemption from the definition of ``organic liquid'' for
gasoline (including aviation gasoline), kerosene (No. 1 distillate
oil), diesel (No. 2 distillate oil), asphalt, and heavier distillate
oils and fuel oils in 40 CFR 63.2406 of the Organic Liquid Distribution
National Emissions Standard for Hazardous Air Pollutants (NESHAP), 40
CFR part 63, subpart EEEE (OLD MACT) include the use of toluene as a
fuel in the inorganic chemical process that manufactures titanium
dioxide (TiO2) at the DuPont Company (DuPont) of Wilmington,
Delaware?
A: No. EPA concludes that the OLD MACT applies to the storage and
transfer of toluene used as fuel in the production of TiO2.
The exemption in 40 CFR 63.2406(3)(i) in the definition of ``organic
liquid'' applies only to those expressly listed liquids. Because
toluene is an organic liquid and is not gasoline, kerosene, diesel,
asphalt, or a heavier distillate oil or fuel oil, it is not eligible
for the exemption under 40 CFR 63.2406(3)(i) merely because it may be
used as a fuel.
Abstract for [M080011]
Q: Does EPA allow a facility to use multiple standard batches to
define a process within a single miscellaneous chemical manufacturing
process unit (MCPU) under 40 CFR part 63, subpart
[[Page 80396]]
FFFF, National Emission Standards for Hazardous Air Pollutants:
Miscellaneous Organic Chemical Manufacturing (the MON rule)?
A: EPA finds that a facility may request that EPA exercise its
authority under 40 CFR 63.10(f) to modify the recordkeeping and
reporting requirements in the MON rule and allow multiple standard
batches per process. Facilities can request approvals of alternative
recordkeeping and reporting in their precompliance reports. [See 40 CFR
63.2520(c)]. Alternatively, requests submitted after the due date of
the precompliance report (i.e., after November 13, 2007) may be
submitted under 40 CFR 63.10(f).
Abstract for [M080012]
Q1: Which Standard Industrial Classification (SIC) code applies to
the glucosamine hydrochloride production process at Cargill
Incorporated in Eddyville, Iowa?
A1: The appropriate SIC code for the glucosamine hydrochloride
production process is 289, Miscellaneous Chemical Products.
Q2: Is the process subject to 40 CFR part 63, subpart FFFF, the
National Emission Standards for Hazardous Air Pollutants: Miscellaneous
Organic Chemical Manufacturing (MON) Rule?
A2: Yes. The glucosamine hydrochloride production process is
subject to the MON Rule.
Q3: If this process is not subject to the MON Rule, is it subject
to the Pharmaceuticals NESHAP or another NESHAP?
A3: No, the facility is not subject to the Pharmaceuticals NESHAP
or another NESHAP.
Abstract for [M080013]
Q. Is the process by which the Spartech Polycast facility in
Stamford, Connecticut, manufactures poly methyl methacrylate (PMMA)
acrylic sheet subject to 40 CFR part 63, subpart FFFF?
A. Yes. Spartech's operations produce a material (PMMA) classified
using Standard Industrial Classification (SIC) code 282 or The North
American Industry Classification System (NAICS) NAICS code 325, and its
operations meet all the other criteria for MACT subpart FFFF to apply.
Abstract for [M080014]
Q: Does EPA approve the use at Dow Chemical's Midland, Michigan,
facility of the results of performance tests conducted on three thermal
treatment units under 40 CFR part 63, subparts GGG and MMM, in lieu of
conducting an initial compliance demonstration for 40 CFR part 63,
subpart FFFF (the MON)?
A: Yes. EPA approves the use of these previously conducted
performance tests as the initial compliance demonstration for the MON,
based in part on Dow Chemical's use of test methods referenced in MACT
subpart FFFF and its declaration that no significant process changes
have occurred since these tests.
Abstract for [M080016]
Q1: Does EPA approve Dow AgroSciences' (DAS) request to monitor the
liquid temperature of its condensers at its Harbor Beach, Michigan,
facility as an alternative to measuring the exhaust gas temperature
when demonstrating initial compliance with 40 CFR part 63, subpart GGG
(the Pharma-MACT)?
A1: No. In regards to the initial compliance demonstration for
process condensers under MACT subpart GGG, EPA will not approve DAS's
request to monitor the liquid temperature as an alternative to
monitoring the exhaust gas temperature because DAS started operating
its condensers before the compliance date, and it did not present
sufficient technical justification for the alternative method.
Q2: Does EPA approve DAS's request to comply with the 20 ppmv
outlet concentration limit under Sec. 63.1254(a)(1)(ii)(A) without
calculating uncontrolled hazardous air pollutant emissions from all
emission episodes using the equations specified in Sec.
63.1257(d)(2)(i), or developing an engineering assessment as allowed in
Section 63.1257(d)(2)(ii), or developing an emission profile as
required by Sec. 63.1257(b)(8)(ii)?
A2: No. In regards to complying with the 20 ppmv outlet
concentration limit under 40 CFR 63.1254(a)(1)(ii)(A), EPA will not
approve DAS's request to forgo calculating uncontrolled emissions,
developing an engineering assessment, or developing an emission profile
because the alternative standard, at Sec. 63.1254(c), is the only
process-vent compliance option for the Pharma-MACT that does not
require calculation of uncontrolled emissions because it requires
continuous monitoring through a continuous emission monitoring system
(CEMS). As DAS does not employ a CEMS, the only way it can ensure
compliance with 40 CFR 63.1254(a)(1)(ii)(A) is if it calculates
uncontrolled emissions and develops an emission profile under worst-
case conditions.
Abstract for [M080017]
Q: Does EPA approve at Dow Chemical Company's Midland, Michigan,
facility, the use of the results of performance tests conducted on
three thermal treatment units per 40 CFR part 63, subparts GGG and MMM,
in lieu of conducting an initial compliance demonstration for 40 CFR
part 63, subpart FFFF (the MON)?
A: Yes. EPA approves the use of these previously conducted
performance tests as the initial compliance demonstration for the MON,
based on Dow's use of test methods referenced in 40 CFR part 63,
subpart FFFF and statement that no significant process changes have
occurred since these tests.
Abstract for [M080018]
Q: Does EPA approve alternative test methods, monitoring, and work
practice standards under 40 CFR part 63, subpart N, for Finishing
Innovation's proposed new hard chrome electroplating tank in Warsaw,
Indiana? The proposed new tank will be equipped with an Emission
Elimination Device (EED), or formerly known as the Merlin Cover, which
is a patented system which totally encloses the chrome tank while
plating takes place.
A: Yes. EPA approves the proposed alternative test method,
monitoring procedures and work practices consistent with previous
approvals. EPA's Office of Air Quality Planning and Standards (OAQPS)
approved an alternative test method utilizing a smoke generation
device. This device would be ignited and placed inside the EED and the
absence of leaking smoke confirmed to demonstrate that the EED
completely encloses the atmosphere over the chrome electroplating tank.
EPA Region 5 has also approved alternative monitoring requirements and
work practices to monitor continuous compliance of the EED and to
ensure that it maintains compliance.
Abstract for [M080019]
Q: Does J.L. French Corporation's variance request letter contain
adequate information for the EPA to approve a request for waiver of
initial performance tests as well as all subsequent performance tests
for the existing aluminum scrap shredders located at J.L. French
Corporation's Gateway and Taylor secondary aluminum production
facilities in Sheboygan, Wisconsin?
A: No. EPA finds that based on the information submitted to the
EPA, we cannot approve J.L. French Corporation's request for waiver of
initial performance tests, as well as all subsequent performance tests
for the existing aluminum scrap shredders. For the EPA to make an
informed decision either approving or denying such a request, J.L.
French Corporation's
[[Page 80397]]
application for waiver of performance tests must be accompanied by a
comprehensive compliance status report proving compliance with the
relevant aluminum scrap shredder standards at 40 CFR part 63, subpart
RRR. In addition, 40 CFR 63.7(h)(3)(iii) provides that any application
for a waiver of a performance test shall include information justifying
the owner or operator's request for a waiver, such as the technical or
economic infeasibility, or the impracticality, of the affected source
performing the required test.
Abstract for [M080020]
Q: Does EPA approve a change to Viscofan's (formerly Teepak)
alternative monitoring plan under 40 CFR part 63, subpart UUUU,
originally approved in February 2005 at its facility in Danville,
Illinois? Viscofan would like to replace one of its GC/PID instruments
with a new Baseline-MOCON, Incorporated Model 8900 GC/PID to measure
hydrogen sulfide and carbon disulfide.
A: Conditional. EPA has determined that it is acceptable under MACT
subpart UUUU for Viscofan to perform a carrier gas (zero) and a single
upscale gas Quality Control (QC) check on a daily basis for each
chemical monitored.
However, Viscofan must still do a full linearity-type calibration
(zero and at least three upscale gas concentrations) initially and at
least quarterly thereafter for each chemical monitored.
Abstract for [Z080003]
Q: Does EPA allow modification in the existing vinyl chloride
alternative monitoring plan under 40 CFR part 61, subpart F, for
Lubrizol Advanced Material's polyvinyl chloride plant in Louisville,
Kentucky?
A: Yes. Based upon a statistical analysis presented by Lubrizol,
EPA finds that there are only minor differences between individual and
composite resin samples that the company analyzes on a monthly basis
under NESHAP subpart F. Therefore, EPA waives the requirement to
compare the results of individual and composite samples on a monthly
basis.
Abstract for [0800017]
Q: Does EPA approve an alternative opacity monitoring procedure,
which consists of monitoring the secondary power input to the
electrostatic precipitator (ESP), for a boiler at the U.S. Sugar
facility in Clewiston, Florida, which is subject to 40 CFR part 60,
subpart Db?
A: No. Because NSPS subpart Db was modified to allow the use of a
particulate matter continuous emission monitoring system (PM CEMS) as
an alternative to the use of a continuous opacity monitoring system
(COMS), EPA finds that there is no justification for now allowing the
use of parametric monitoring of the ESP. Therefore, unless U.S. Sugar
can demonstrate that a PM CEMS is not a viable alternative to a COMS,
EPA does not approve the request to use parametric monitoring, which is
a less accurate and reliable alternative.
Abstract for [0800018]
Q: Does EPA approve changes to monitoring and operational
requirements for the landfill operated by Environtech in Morris,
Illinois, under 40 CFR part 60, subpart WWW?
A: Conditional. EPA finds that it needs to approve alternatives to
monitoring and operational requirements that are part of the design
plan, and EPA's Office of Air Quality Planning and Standards
(OAQPS)needs to approve such alternative test methods. However, the
Illinois Environmental Protection Agency (IEPA) has the authority to
approve non-monitoring, non-operational changes to the design plan. EPA
refers to several previous determinations on the Applicability
Determination Index (ADI) with ADI Control Numbers 03000120, 0400033,
0600062, 0600063, and M040028, and the modifications of September 21,
2006, to 40 CFR part 60 (71 FR 55127) in addressing many specific
requests.
Abstract for [0800019]
Q: Does EPA approve changes to monitoring and operational
requirements for the landfill operated by LandComp in Ottawa, Illinois,
under 40 CFR part 60, subpart WWW?
A: Conditional. EPA finds that it needs to approve alternatives to
monitoring and operational requirements that are part of the design
plan, and EPA's Office of Air Quality Planning and Standards (OAQPS)
specifically within EPA needs to approve alternative test methods.
However, the Illinois Environmental Protection Agency (``IEPA'') has
the authority to approve non-monitoring, non-operational changes to the
design plan. EPA refers to a several previous applicability
determinations on the Applicability Determination Index (ADI) with ADI
Control Numbers 03000120, 0400033, 0600062, 0600063, and M040028, and
the modifications of September 21, 2006, to part 60 (71 Federal
Register 55127) in addressing many specific requests.
Abstract for [0800020]
Q: Does EPA approve changes to monitoring and operational
requirements for the landfill operated by Lee County in Dixon,
Illinois, under 40 CFR part 60, subpart WWW?
A: Conditional. EPA finds that it needs to approve alternatives to
monitoring and operational requirements that are part of the design
plan, and EPA's Office of Air Quality Planning and Standards (OAQPS)
needs to approve alternative test methods. However, IEPA has the
authority to approve non-monitoring, non-operational changes to the
design plan. EPA refers to several previous applicability
determinations on the Applicability Determination Index (ADI) with ADI
Control Numbers 03000120, 0400033, 0600062, 0600063, and M040028, and
the modifications of September 21, 2006, to part 60 (71 FR 55127) in
addressing many specific requests.
Abstract for [0800021]
Q: Does EPA allow the gas-fired process heater (new 77F-1)
installed at the Marathon Ashland Petroleum refinery (Marathon) in
Robinson, Illinois, to be exempt from 40 CFR part 60, subpart Ja, given
that the heater was purchased in 2001 but never installed?
A: No. Given the six-year gap since the purchase of the heater and
its incomplete fabrication, and given further that Marathon has not
started the bidding process to ship and install the process heater, EPA
finds that Marathon has not undertaken a continuous program of
construction and has not ``commenced construction'' of an ``affected
facility'' on or prior to May 14, 2007. Thus, when the heater is
constructed at the refinery and upon the effective date of NSPS subpart
Ja, the heater will be subject to NSPS subpart Ja.
Abstract for [0800022 & 0800023]
Q: Does EPA allow the Milam Recycling and Disposal facility (Milam)
in East Street Louis, Illinois, to obtain a higher operating
temperature for landfill gas extraction wells MW 39 and MW58 under 40
CFR part 60, subpart WWW?
A: Yes. The NSPS requires that each interior wellhead in the
collection system operate with a landfill gas temperature less than 131
degrees Fahrenheit. The facility may request a higher operating
temperature under NSPS subpart WWW if supporting data demonstrate that
the elevated temperature does not cause fires or inhibit anaerobic
decomposition by killing methanogens. As Milam has
[[Page 80398]]
submitted such data, EPA approves a higher operating temperature of 140
degrees Fahrenheit for well MW39 and MW58.
Abstract for [0800024]
Q: Does EPA approve an alternative timeline, under 40 CFR part 60,
subpart WWW, to correct oxygen exceedances at leachate cleanout riser
LCO-02A at the Veolia Orchard Hills Landfill in Davis Junction,
Illinois?
A: Yes. EPA approves the alternative timeline under NSPS subpart
WWW. Veolia Orchard Hills Landfill may have until 45 days of the
initial exceedance to correct the oxygen exceedances.
Abstract for [0800025]
Q: Does EPA allow the Owens-Brockway Glass Container facility in
Lapel, Indiana, to measure the bridgewall optical temperature (BWOT),
under 40 CFR part 60, subpart CC, three times per shift instead of
installing and operating a continuous opacity monitor on its Furnace
Number 32?
A: No. NSPS subpart CC requires that continuous parameter
monitoring systems complete a minimum cycle of operation (sampling,
analyzing and data recording) every 15 minutes. EPA determines that if
the BWOT cannot be measured continuously, then it is not an appropriate
alternative monitoring parameter to opacity, and the facility should
install a COM.
Abstract for [0800026]
Q: Does EPA approve an alternative timeline under 40 CFR part 60,
subpart WWW, to correct oxygen exceedances at Veolia's Valley View
Landfill in Decatur, Illinois?
A: Yes. EPA approves an extension of up to 53 days from the date of
the initial exceedance to bring wells 19R and 26R into compliance with
the oxygen concentration standard under NSPS subpart WWW.
Abstract for [0800027]
Q1: Does EPA consider indirect-fired dryers used in the ethanol
industry subject to 40 CFR part 60, subparts Db or Dc?
A1: EPA finds that both NSPS subparts Db and Dc apply to indirect-
fired dryers as they use the process of drying in a closed steam loop
system with an integrated thermal oxidizer to transfer heat across a
physical barrier. In the indirect heating method being used, they meet
the definition of a steam generating unit under 40 CFR 60.41b and
60.41c.
Abstract for [0800028]
Q1: Does EPA considered any of the material used as a feedstock on
the Spherical Catalyst Manufacturing (SCM) Line 1 at UOP's Shreveport,
Louisiana, plant, a ``mineral'' as term is used in the definition of
``mineral processing plant,'' under NSPS subpart UUU?
A1: No. EPA finds that none of the feed materials used on SCM Line
1 (pure aluminum, hydrochloric acid, and/or aluminum hydroxychloride
solution) is a ``mineral,'' as the term is used in the definition of
``mineral processing plant,'' under at 40 CFR 60.731.
Q2: Does synthetic alumina produced on the Spherical Catalyst
Manufacturing (SCM) Line 1 at UOP's Shreveport, Louisiana, plant, using
a combination of pure aluminum, hydrochloric acid, and/or aluminum
hydroxychloride solution, meet the definition of a ``mineral,'' as the
term is used in NSPS CFR subpart UUU in the definition of the affected
facility: each calciner and dryer at a ``mineral processing plant,''
located in NSPS subpart UUU at 40 CFR 60.730?
A2: No. EPA finds that the synthetic alumina produced on SCM Line 1
does not meet the definition of ``mineral.''
Q3: Is SCM Line 1, located at UOP's Shreveport, Louisiana, plant,
processing a ``mineral,'' as the term is used in 40 CFR part 60,
subpart UUU, or producing a ``mineral,'' as the term is used in the
definition of the affected facility (each calciner and dryer at a
``mineral processing plant'') in subpart UUU, potentially subject to
NSPS part 60, subpart UUU?
A3: No. EPA finds that SCM Line 1 cannot be subject to subpart UUU,
because it neither processes a ``mineral,'' nor does it produce a
``mineral,'' and, therefore, it does not meet the NSPS subpart UUU
definition of a ``mineral processing plant''
Abstract for [0800029]
Q: Does EPA allow Louisville Gas and Electric (LG&E) to substitute
particulate matter continuous emission monitoring systems (PM CEMS) for
continuous opacity monitoring systems (COMS) under 40 CFR part 60,
subpart D, on Units 3 and 4 at its Mill Creek Station in Louisville,
Kentucky?
A: Yes. Because EPA believes that PM CEMS will be superior to COMS
for verifying compliance with the applicable particulate emission limit
for Units 3 and 4, LG&E's alternative monitoring proposal under NSPS
subpart D is approved, provided that a number of conditions outlined in
the approval are met.
Abstract for [0800030]
Q: Does EPA allow the Kentucky Utilities Company (KU) to substitute
particulate matter continuous emission monitoring systems (PM CEMS) for
continuous opacity monitoring systems (COMS) under 40 CFR part 60,
subpart D, on Unit 3 at its Mill Ghent Station in Ghent, Kentucky?
A: Yes. Because EPA believes that PM CEMS will be superior to COMS
for verifying compliance with the applicable particulate emission limit
under NSPS subpart D for Unit 3, EPA approves KU's alternative
monitoring request, provided that a number of conditions outlined in
the EPA response are met.
Abstract for [0800031]
Q: Does the replacement of the gas turbine at the Bristol-Myers
Squibb facility in New Brunswick, New Jersey, constitute reconstruction
under 40 CFR part 60, subpart KKKK?
A: Conditional. For the purpose of NSPS subpart KKKK, EPA finds
that the affected facility is not limited to the turbine itself. It is
not clear from the submittal what the fixed capital cost of the new
components is as compared to a similar entirely new facility. Costs
outside of the affected facility, such as the building, air pollution
control, testing, and monitoring equipment, site preparation, removal
of the old turbine, and contingency costs should not be included.
Abstract for [0800032]
Q: Does EPA approve the use of sensory means (i.e., visual,
audible, or olfactory), as an alternative, under 40 CFR part 60,
subparts VV and VVa, to using EPA Method 21 for the identification of
leaks from equipment in acetic acid service at the Eastman Chemical
Company facility in Columbia, South Carolina?
A: Yes. EPA finds that the proposed alternative is acceptable under
NSPS subparts VV and VVa. Monitoring results provided by Eastman
indicate that leaks from equipment in acetic acid service are more
easily identified through sensory methods than by using Method 21
because of the physical properties (high boiling point, high
corrosivity, and low odor threshold) of acetic acid and the process
conditions at the plant.
Abstract for [0800033]
Q: May Air Products and Chemicals, Inc. (Air Products) use the
process monitor as the primary method to measure hydrogen sulfide
(H2S) for two furnaces located within the ExxonMobil Joliet,
Illinois, refinery, and eliminate the previously stipulated alternative
monitoring plan (AMP) conditions that require random H2S
grab sampling, under the New Source Performance
[[Page 80399]]
Standards for Petroleum Refineries, 40 CFR part 60, subpart J.
A: No. EPA finds that the conditions of the AMP cannot be revised,
because monitoring a process parameter is not a substitute for
H2S grab sampling. Please refer to a previous EPA approved
AMP available on the Applicability Determination Index (AD)) under ADI
Control Number 0100037.
Abstract for [0800034]
Q: Does EPA approve a boiler derate proposal , under 40 CFR part
60, subpart Dc, based on changes made to the natural gas-fired boiler
at the facility located in Dearborn, Michigan?
A: Yes. EPA approves this proposal under NSPS subpart Dc, as it
will reduce the capacity of the boiler and will comply with EPA's
policy on derates.
Abstract for [0800035]
Q: Does EPA approve an alternative compliance timeline under 40 CFR
part 60, subpart WWW, to correct a pressure exceedance at the
Livingston Landfill, Well GW10, located in Pontiac, Illinois?
A: No. On November 20, 2007, the GW10 well at Livingston Landfill
showed a positive pressure reading. On December 3, 2007, Livingston
requested an extension to bring the well into compliance. However,
according to a phone conversation between EPA and Cornerstone
Environmental Group on January 4, 2008, the well had achieved
compliance within 15 days of the initial exceedance. Therefore, EPA
determines that an alternative compliance timeline was not required.
Abstract for [0800036]
Q: Does EPA concur with Michigan Consolidated Gas Company
(MichCon), a solely owned subsidiary of DTE Energy LLC, that 40 CFR
part 60, subpart KKK, does not apply to the recent expansion project of
a propane refrigeration plant at MichCon's Belle River Mills facility?
A: No. EPA determines that NSPS subpart KKK is applicable to the
recent expansion project because the propane refrigeration system uses
a process that extracts ``natural gas liquids.'' Thus, the facility
meets the definition of a natural gas processing plant set forth in 40
CFR 60.631.
Abstract for [0800037]
Q: Does EPA approve an alternative monitoring plan, under 40 CFR
part 60, subpart UUU, to monitor the nozzle pressure of a Venturi
scrubber instead of the pressure loss of the gas stream through the
Venturi scrubber at 3M's Cottage Grove, Minnesota, facility?
A: Yes. EPA finds that the 3M Company has demonstrated that the
nozzle pressure is a reasonable alternative under NSPS subpart UUU to
the pressure loss of the gas stream through the Venturi scrubber.
Abstract for [0800038]
Q: Does EPA approve an alternative timeline under 40 CFR part 60,
subpart WWW, to correct oxygen exceedances at Veolia Orchard Hills
Landfill's Leachate Recirculation Line LRW-12, located in Davis
Junction, Illinois?
A. Yes. On February 14, 19, and 26, 2008, Veolia's leachate
recirculation line, LRW-12, exceeded the 5 percent oxygen concentration
standard. EPA approved an alternate timeline under NSPS subpart WWW for
Veolia to correct the oxygen exceedances until May 14, 2008. EPA finds
that if the oxygen standard cannot be met by May 14, 2008, the landfill
will need to apply to have the well decommissioned. If Illinois EPA
does not approve such decommissioning, and Veolia cannot achieve an
oxygen concentration below 5 percent by May 14, 2008, then Veolia must
have the gas collection system expanded by 120 days of the initial
exceedance.
Abstract for [0800039]
Q: Does EPA approve an alternative timeline under 40 CFR part 60,
subpart WWW, for Roxana Landfill, in Roxana, Illinois, to correct
positive pressure at the wells number 6, 7, 8, 18, 20, 22, 23, 24, 38,
39, 40, 41, 42, 43, 44, 45, and 46 wells?
A: Yes. EPA approves Roxana's proposed alternative timeline under
NSPS subpart WWW. However, if Roxana cannot measure and achieve
negative pressure without excess air infiltration at the wells number
6, 7, 8, 18, 20, 22, 23, 24, 38, 39, 40, 41, 42, 43, 44, 45, and 46 by
the alternative compliance date, Roxana must expand the gas collection
system within 120 days of the initial exceedances.
Abstract for [0800040]
Q: Does EPA approve alternative operational standards and
p