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8.34
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
WASHINGTON, D.C. 20460
FEB 3 1989
OFFICE OF
AIR AND RADIATION
MEMORANDUM
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SUBJECT: Determination for Davidson Exterior Trim/Textron
FROM: John S. Seitz, Director
Stationary Source Compliance Division
Office of Air Quality Planning and Standards
TO: Winston A. Smith, Director
Air, Pesticides and Toxics Management Division
Region IV
On October 14, 1988 you forwarded to this division a request regarding
the BACT determination for the Davidson Exterior Trim/Textron facility in
Georgia. We have coordinated a response to your request with the New Source
Review Section in AQMD, the Chemical Application Section in ESD, and the Air
Enforcement Division in OECM. The following responses to your questions are
provided:
- Does Davidson Exterior present "unique and convincing" arguments which
would justify elimination of add-on spray booth and/or over controls as
BACT?
While Davidson has supplied data on the control cost, cost
effectiveness, and percent increase in the cost per unit of product,
they have not presented an argument as to why the control cost is
unreasonable. It also appears that there are control alternatives
available which Davidson has not explored (see response to question 2 &
3 below). Therefore, we agree that Davidson Exterior has failed to
make a case for rejecting as BACT the add-on controls in question.
- Are there other fascia plants which have been required to install both
spray booth and oven controls?
We know of no other fascia plants which have been required to install
both spray booth and oven controls. The General
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Motors parts plant in Oshawa, Ontario, Canada has recently installed an
exhaust air recirculation and VOC control (incineration) system on the
clear coat portion of the fascia spray booths.
- Has EPA established spray booth and/or oven controls as BACT at fascia
painting operations?
Bake oven exhaust controls have been required in several BACT/LAER
permits for fascia painting (Subaru-Isuzu, Dupont, Saturn, etc.).
Spray booth exhaust controls have not been required in BACT/LAER
permits for fascia painting. The number of controlled spray booths is
growing (e.g., automobiles, aerospace, metal parts), and the cost of
control is becoming lower with experience and the development and
demonstration of new technologies (e.g., recirculation, control
equipment for low VOC concentration exhaust streams). Spray booth
exhaust controls, therefore, must receive serious consideration in
current and future permitting of fascia painting operations.
- Were the oven controls installed on the fascia operations at the
Subaru/Isuzu facility, located in Lafayette, Indiana, the result of a
BACT evaluation or necessitated for some other reason?
The bake oven exhaust controls at Subaru-Isuzu were part of the BACT
demonstration.
- If the arguments presented by Davidson Exterior do not constitute a
"unique and convincing" basis for rejection of controls, what would EPA
consider to be valid criteria for rejection of the controls?
Three criteria which should be asked when reviewing permits in which
more stringent levels of control have been rejected as BACT are
discussed below:
i) If another similar source has adopted certain emission controls,
why can't this applicant? Where similar units have adopted a
particular level of emission control or control technology, the
applicant should justify on technical, environmental, or economic
ground why they cannot also adopt that particular control system or
otherwise meet that level of control. This analysis should focus on
the differences (if any) between the two sources (e.g., differences in
raw material costs or control costs).
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ii) Why is the economic impact of a level of control unreasonable?
Where a permit applicant claims that emission control costs are
unreasonable, the burden of showing why the cost are unreasonable is on
the applicant. Some possible parameters for judging the reasonableness
of a control level could be the percent of the total cost of a
construction or modification project, cost effectiveness per ton), or
percent cost increase per unit of product. Again, other similar
sources that have adopted a particular level of control may provide a
useful benchmark against which to compare the claimed economic impact
of emission controls. However, control cost data and cost
effectiveness calculations likely do not, standing alone, provide a
convincing argument against adopting a potential BACT level. For
example, simply stating that it is infeasible to meet a particular cost
per tan of pollutant controlled is not adequate; the reason must be
explicity explained to EPA, the permitting agency, and the public. The
applicant should look at this cost in terms of typical control cost for
other sources of this pollutant. The costs of control for similar
sources is addressed in #i above.
iii) Based on the reviewer's experience in reviewing control cost
estimates and cost effectiveness calculations for a particular
pollutant and source category, do the cost data provided by the
applicant seem credible? In other words, are the cost estimates within
the range of costs you would expect to see for that particular type of
source or pollutant? If a cost or cost effectiveness estimate strikes
you as being too high, you should ask the applicant to explain why
their emission control costs would be higher than those documented for
a similar source.
- Would Headquarter's support a Section 167 order, issued by Region
IV, if it is determined that Davidson Exterior has not installed or
proposed to install BACT?
Consistent with the July 15, 1988 guidance on procedures to follow when EPA
finds a Deficient New Source Permit, a deficient BACT analysis is cause for
expeditious (within 30 days of permit receipt) issuance of a Section 167
order in SIP-approved programs. However, the ultimate decision whether to
proceed with enforcement action in this or any other case depends, in large
part, upon all the specifics of the particular cases. These include, among
others:
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1) The time and manner in which EPA has informed the applicant and
the permitting authority of alleged defects in the permit, and of
the consequences of a failure to correct those defects.
2) The amount of time between permit issuance and the commencement of
enforcement action.
3) whether the applicant has entered into construction contracts,
begun actual construction, or otherwise acted in reliance on the
State-issued permit.
4) Plus, for SIP-approved States, the content of the State
regulations and relevant Federal Register notices.
I apologize for the delay in providing this response. If you have any
questions, please contact Gary McCutchen in AQMD (FTS-629-5592) regarding
responses #1 & 5, Dave Salman in ESD (FTS-629-5417) regarding responses #2-
4, and Sally Farrell of my staff (FTS-382-2875) regarding response #6.
cc: Wayne Aronson, Region IV
Mark Armentrout, Region IV
Gary McCutchen, AQMD
Sam Duletsky, AQMD
Jim Berry, ESD
Dave Salman, ESD
Judy Katz, OECM
NSR Contacts, Region I-X
Greg Foote, OGC |