United States
Environmental Protection
Agency	 	
Air and Energy Engineering
Research Laboratory
Research Triangle Park NC 27711
Research and Development
EPA/600/S2-88/071  Sept. 1989
 Project Summary
 Volatile  Organic
 Compound  and  Participate
 Emission  Studies of AF  Paint
 Booth  Facilities:   Phase  I
 Jacqueline Ayer and Dean Wolbach
  Results of volatile organic  com-
pound (VOC)  and participate emis-
sion studies at three Air Force  spray
paint facilities are presented. It was
found that all  three facilities (one at
McClellan AFB CA and two at Travis
AFB CA) were out of compliance for
VOC emissions.  The possibility of
reducing VOC  emissions with  recir-
culation  modifications and  various
control  strategies  is  discussed.
Specific  recommendations for  emis-
sion reductions pertaining to  each
facility are presented.
  This Project  Summary was devel-
oped by EPA's Air and Energy  Engi-
neering  Research  Laboratory, Re-
search Triangle Park, NC, to announce
key findings of the research project
that is fully documented in a separate
report of the same title (see Project
Report ordering information at back).

Objective
  This study  presents the  results of
volatile organic  compound (VOC) and
particulate emission surveys performed
at three Air Force painting facilities. The
three facilities -- one at McClellan AFB
Building 655 and two at Travis AFB build-
ings 550  and 1014 -- did not meet local
VOC emission  standards. This  report
discusses the  possibility of reducing
these  emissions with recirculation
modifications and various VOC reduction
and control strategies.
  Although  VOC emissions  from paint
spray booths can be controlled by add-on
control systems, control is expensive for
present air flow rates. The  use  of air
recirculation within the spray booth can
reduce the cost of VOC emission controls
by reducing the quantity of air which re-
quires processing. Recirculation systems
were designed for two of the painting
facilities included in this study  In design-
ing the systems, various criteria such as
paint booth  VOC concentrations and
health and safety standards were consid-
ered. Add-on  VOC  emission control
systems  which  can  be  used in
conjunction with the recirculation system
are evaluated  in this study.  The devices
of interest are a solvent incineration sys-
tem and an activated carbon adsorption
bed.  The VOC removal efficiency, initial
capital investment, and operating  costs
for both of these technologies are discus-
sed.

Background
  The Air Force  uses  a  number of
solvents and  solvent-based coatings  in
many routine operations that are required
to maintain aircraft-related equipment.
Activities which result in the emission of
large quantities of VOCs include  metal
cleaning, painting, paint removal, fuel
storage and transfer, and industrial waste
treatment. As a result of these operations,
significant quantities of  VOCs are
released  into  the atmosphere. For this
reason,  Air Force operations comprise
one  of the  VOC source categories
regulated by the Clean Air Act and state
and local laws.
  Solvent-based epoxy primers and sol-
vent-based polyurethane  topcoats are
normally used by  the Air Force for paint-
ing aircraft. Methylethyl ketone, isopropyl

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alcohol, toluene,  lacquer thinner, and
aliphatic polyurethane thinner are the sol-
vents generally involved in painting. Cur-
rently the solvents, primers, coatings for
corrosion control, and aerospace top-
coats used by the Air Force exceed VOC
emission limits established by both fed-
eral and state laws.  The statutory dead-
line to comply with both state and federal
laws was December 31, 1987.
  The  study of VOC and  particulate
emissions  and possible  reduction strat-
egies at the three Air Force painting facil-
ities took place  between June and Sep-
tember  1987. Painting  operations  at
McClellan  AFB  Building  655 were  ob-
served between June  1  and 5.  Painting
operations at Travis AFB  Buildings 550
and  1014 were  observed between June
16 and 19, and June 24 and 30, respec-
tively.

Project Description
  The  project was conducted  in two
steps. Step 1 involved characterizing the
VOC and particulate emissions from the
painting facilities included in this study.
Step 2  was to  make  recommendations,
based  on the data collected in Step 1, of
         viable  VOC  emission  reduction  and
         control options for each facility.
           Step 1 was accomplished by observing
         the paint operations  occurring  at  each
         facility, and  sampling for  organics  and
         particulates both inside and  outside the
         paint booth. The sampling methods used
         to characterize the emissions were Na-
         tional  Institute of Safety  and  Health
         (NIOSH)  500,  NIOSH 1300, Modified
         Method 5, anemometer volume flow, EPA
         Method 2 volume flow, ST-7, and Method
         25A. In addition, records  of paint  usage
         rates  and paint booth operations  were
         kept.  At McClellan AFB,  water  samples
         were drawn from the water curtain sumps
         which remove  particulate  from  the
         exhaust flow.
           Step 2 was accomplished by analyzing
         the data and  developing  possible VOC
         emission control  strategies for  each
         painting facility included in this study.


         Conclusions and
         Recommendations
         •  All three painting facilities included  in
            this study  failed to meet  applicable
            VOC emission standards.
The  adoption of more efficient  p<
application  methods  is a viable  V
emission reduction strategy.
Paint booth recirculation modificatk
associated with an  add-on  conl
device would result in significant  V
emission reductions.
A recirculation system could be ins
led at the McClellan AFB  Building (.
paint facility at an approximate cosl
$47,000.  The  bleed-off volui
required  to  maintain  the  VI
concentration below established saf
limits is 1,500 scfm (0.71 sm3/sec).
A recirculation system could be ins
led  at  the  Travis AFB Building  1(
painting facility at an  approximate c
of $33,000.  The  bleed-off  volui
required  to  maintain   the  VI
concentration below established saf
limits is 860 scfm (0.41  sm3/sec).
Recommendations  specific to  e«
site  regarding safe and1 efficient  pi
booth operation
 Jacqueline Ayer and C. Dean Wolbach are with Acurex Corporation. Mountain View,
  CA 94039.
 Charles H. Darvin  is the EPA Project Officer (see below).
 The  complete report,  entitled "Volatile  Organic Compound  and  Particulate
  Emission Studies of AF Paint Booth Facilities: Phase I," (Order No. ADA 198092;
  Cost: $21.95, subject to change) will be available only from:
         National Technical Information Service
         5285 Port Royal Road
         Springfield, VA 22161
         Telephone: 703-487-4650
 The EPA Project Officer can be contacted at:
         Air and Energy Engineering Research Laboratory
         U.S. Environmental Protection Agency
         Research Triangle Park, NC27711
 United States
 Environmental Protection
 Agency
Center for Environmental Research
Information
Cincinnati OH 45268
 Official Business
 Penalty for Private Use $300

 EPA/600/S2-88/071
      000085833    PS
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