Reducing Volatile Emissions in the Fiber
Reinforced Plastics Industry (FRP)
Most FRP processors
are major sources of volatile emissions. The emissions from
FRP processing facilities include styrene, the volatile component
of polyester resin and gelcoat; and acetone, a solvent used
to clean tools and other surfaces contaminated with resin.
FRP industries benefit
by reducing volatile emissions. These benefits include: |
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Less concern about Occupational
Safety and Health Administration (OSHA) regulations related
to worker exposure to chemicals, especially styrene. |
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Less concern about regulation
of air pollutants as a result of the 1990 Clean Air Act
Amendments (CAAA), especially the recently proposed Maximum
Achievable Control Technology (MACT) standards. |
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Reduced risk of fires caused
by high concentrations of chemicals in the workplace. |
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Fewer emissions implies
better raw materials use, improving the bottom line. |
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Reduced disposal cost of
spent solvents as hazardous waste. |
This fact sheet describes the ways in which
FRP operations may obtain these benefits.
Process
Change Considerations
No single option is likely to replace
the plant wide use of solvent or completely eliminate
the source of volatile emissions. Examine alternatives
that combine several options. When considering a substitute,
keep in mind the following: |
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Will a new waste stream
be created? If so, how will it be handled? |
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Do the new materials pose
a worker health or safety risk? |
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What will the effect be
on product quality and production levels? |
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What experience have others
in the industry had with the alternative technology? |
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How much employee training
will be required for successfully implementing a substitute? |
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What regulations
need to be considered? |
Reducing
Styrene Emissions
Styrene emissions result primarily
from materials application and laminate cure. While applying
materials, styrene emissions often result from resin atomization
and overspray. Laminate cure often results in high emissions
due to the evaporating liquid. In general, the higher
the styrene content and resin atomization during application,
the higher the emissions. Opportunities for reducing styrene
emissions include: |
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Substitute low-styrene
emission resins. |
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Upgrade resin and gelcoat
application equipment. |
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Convert open-mold processes
to closed-mold processes. |
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Implement a controlled
spraying program. |
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Improve raw
material monitoring through better processing control. |
Low-Styrene Emission
Resins
Low-styrene emission resins are grouped into two general categories
including reduced styrene resins and vapor-suppressed resins.
Reduced styrene resins contain 35
percent or less styrene on a weight basis than conventional
resins. The chemistry of low-styrene resin has low viscosity
and the desired appearance of a final laminate. However, their
viscosity is higher than conventional resins and roll out
over reinforcing material may be tougher. The viscosity is
much more sensitive to temperature fluctuations, which may
require improved temperature control. The cost of low-styrene
resins is comparable to conventional resins. The Unified
Emission Factors developed by the Composites Fabricators
Association (CFA) show
that a decrease in the styrene content
from 40 to 35 percent will reduce styrene emissions by 20
to 50 percent, depending on the application method employed.
Vapor-suppressed resins contain an
additive that forms a barrier inhibiting the release of styrene
during the laminate cure process. In the past, the additives
were wax-like, but problems with secondary bonding limited
their acceptance. The reactivity of the newer vapor suppressing
additives safeguard secondary bonding, which allows crosslinking
to occur within the vapor suppressing film. Appropriate concentration
levels of the additive, ranging from 0.2 to 1.0 percent, are
crucial as high levels reduce effective secondary bonding.
Tests done by BYK-Chemie,
a resin manufacturer, suggest the use of vapor-suppressed
resins reduces styrene emissions in excess of 50 percent.
Upgrading Application
Equipment
Many FRP processors apply resin or gelcoat using conventional
spray equipment, which requires high fluid pressure or compressed
air to create a finely divided spray. All conventional spray
technologies produce misting, which results in overspray.
Transfer efficiency decreases when material misses the mold
surface. Mistingand particularly the resulting oversprayincreases
the surface area of the resin or gelcoat particles exposed
to air during application, causing a higher evaporation rate
which increases emissions.
In order to mitigate these negative effects,
new application equipment technologies have been developed.
These include non-spray and non-atomized technologies, such
as flow coaters and fluid impingement equipment. Non-atomized
technologies are viable in almost all open-molding operations.
Flow coaters are internal mix guns
that produce low-pressure streams of resin. These guns can
be equipped with a glass chopper to simultaneously apply catalyzed
resin and reinforcing media. Because flow coaters rely on
internal mixing of the resin and catalyst, the operator must
periodically flush the mixing chamber with an appropriate
solvent to minimize contamination build-up. Depending on the
solvent used, this may affect hazardous waste generation.
Fluid impingement application equipment
can be either internal or external mix. In both cases, the
resin or gelcoat exits the gun in two low-pressure streams
which cross each other. Their collision creates a fan pattern.
As with the flow coaters, chopped glass can be simultaneously
combined. The Coating Applications Research Laboratory (CARL)
at Purdue University found that the fluid impingement technology
gelcoat system generated 32 percent fewer styrene emissions
than conventional equipment.
To successfully implement non-atomized application
technologies, several issues must be addressed. First, non-atomized
spray appears to wet-out slower than conventional spray. Although
it takes slightly longer to saturate the glass, it will wet-out
quickly once the roll out process begins if the equipment
is adjusted for the appropriate glass-resin ratio. The operator
must be trained on this aspect because the tendency is to
apply excess resin and glass. Secondly, capturing the chopped
glass in the resin stream is another concern. The chop chute
needs to be adjusted more precisely than traditional equipment.
Failure to do so results in a wider distribution than desired.
A final concern is the electrical charge that may occur during
spraying. On the extreme, glass is repelled away from the
resin stream. Either proper grounding of the equipment or
glass roving with a charge opposite of the system's may be
required. It is best to consult the equipment supplier when
addressing this issue.
Converting Closed-Mold
Process
Another alternative is to convert open-mold processes to closed-mold
processes. The closed-mold process not only reduces emissions
but optimizes the glass-resin ratio, producing a higher quality
laminate. The two techniques presented here include vacuum
bagging and resin infusion.
Vacuum bagging technique applies
resin and reinforcement in the traditional manner. Before
the laminate starts to cure, a thin plastic film is placed
over the uncured laminate and a vacuum is drawn over the system.
This creates a pressure of one atmosphere over the laminate
surface and forces excess resin from the system. Vacuum bagging
techniques increase the glass to resin ratio, enhance physical
properties of the laminate and reduce
the amount of resin used. If the bag is not reusable, solid
waste from applying this technique will increase.
Resin infusion technique converts
existing open-molds by fitting a flexible membrane around
the mold perimeter. Reinforcements are tacked into place,
the membrane is sealed around the mold edge and a vacuum is
drawn on the system. The membrane stretches to make contact
with the reinforcing media. A valve is opened and resin is
sucked into and through the reinforcing media. Resin infusion
reduces styrene emissions by eliminating the exposure of liquid
resin to the environment during the manufacturing process.
No overspray and less flashing waste are produced, while a
minimum quantity of resin is used. Resin infusion increases
part quality and part-to-part consistency. Reduced labor helps
justify its large capital expense. Solid waste may increase,
but the membrane can be used multiple times. Waste increase
is typically less than vacuum bagging.
Resin infusion has been successful when
parts require multiple reinforcing layers. For example, Larson
Boats, part of Genmar Holdings in Minneapolis, Minnesota,
makes boat hulls using the Virtual Engineered Composition
(VEC) process. The VEC process is a closed-mold
approach to boat building that incorporates sophisticated
automation to produce high quality high strength parts with
part-to-part weight consistencies within one percent. The
entire molding process is enclosed, reducing styrene emissions
by 77 percent and solid waste by 50 percent.
Implementing Controlled
Spraying Programs
Controlled spraying is an effective work practice that reduces
styrene emissions in conventional open molding processes up
to 25 percent. By minimizing spray gun atomization and reducing
overspray loss, a manufacturer improves the transfer efficiency
of resin or gelcoat. This approach is most effective for operations
using atomization spray equipment, but certain aspects may
benefit operations using non-atomized spray equipment as well.
A controlled spray program is comprised of three elements:
containment flanges around the mold perimeter, spray gun pressure
calibration and spray operator training.
Containment flanges may be designed
for new molds or added to existing mold designs. Masking may
also be applied around the mold perimeter as a temporary flange.
In each case, the flange acts as a barrier to potential overspray,
which is captured and accumulated at the flange. Because resin
and gelcoat particles have less surface area exposed to the
air, styrene emissions are reduced.
Spray
gun pressure calibration is a technique that reduces
tip pressure to the lowest possible point while maintaining
an acceptable spray pattern. This decreases styrene emissions
by decreasing misting. One way to accomplish this is to
apply the CFAs Calibration Procedure: |
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Verify the correct temperature
of the resin and that it has been mixed for the manufacturers
specified amount of time. |
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Verify the spray tip is
in good condition and it is sized appropriately for the
flow rate and fan pattern width for the job. |
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Hold the gun perpendicular,
12 to 18 inches from the floor, and aim it at a disposable
floor covering. |
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Turn pump pressure to
zero and pull the trigger. |
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Slowly begin to increase
the pressure in 10 psi increments until the fan pattern
is adequate. If the fan pattern produces a symmetrical
ellipse, the pressure is optimum. |
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Record this pressure in
the spray gun set up log. |
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Increasing the pressure
above this point results in over atomization, increased
overspray and poor transfer efficiency. |
Operator training is crucial to producing
high quality work and reducing styrene emissions. Precise
spray gun aim is necessary in order to put as much material
into the final part as possible. Operators need to develop
a high level of concentration because application rate and
gun movement determine an even thickness across the part.
The use of a thickness gauge helps ensure proper material
thickness, as well as part-to-part consistency and optimal
material use. When spraying the perimeter, keep within the
area of the containment flange. Overspray that hits the floor
increases styrene emissions.
Improved Process
Control
Robots
A tight labor market allows FRP open-molding processes to
consider the use of robots. A robot with the appropriate automation
is the ultimate in controlled spraying. Robots guarantee proper
positioning of the spray gun and ensures optimized coverage.
Although somewhat capital intensive, these systems produce
parts faster, improve part-to-part consistency, optimize materials
use, reduce plant ventilation requirements and reduce ergonomic
injuries. Some robots are also capable of collecting production
data.
Weight tolerance of parts is greatly improved
resulting in significant material savings. Overall material
use for manual application is higher because excess overspray
and weight difference from part to part will have a larger
statistical spread. For example, if part-to-part weights for
manual application have a spread of +/- 10 percent and robotic
application has a spread of +/- 5 percent, then a robotic
application consuming 1,000 pounds of material per day will
save more than 50 pounds of material.
Material savings, increased rates of production and improved
part quality ensure a quick payback on the system.
Maintenance issues may require additional
training for personnel. On site computer programming and fitting
new products into the process may require extra expertise.
Raw Material Monitoring
Systems
Raw material monitoring systems are electronic devices capable
of delivering real time information concerning resin, glass
and catalyst application. These systems allow processors to
keep track of material used and to achieve part weight goals.
As a result, part-to-part consistency is maintained and overall
material use decreases resulting in fewer emissions. Data
from these systems can be transferred to a computer for improved
costing or record monitoring. A payback of one year or less
is achievable.
Reducing Acetone
Emissions
Acetone is a commonly used solvent for cleaning uncured polyester
resin and gelcoat from tools and contaminated surfaces. In
a typical FRP operation, more than 50 percent of the solvent
used can be lost to air through evaporation. The remaining
spent solvent can be processed on-site to reclaim the acetone
or disposed of off-site as hazardous waste. Still-bottoms
remaining from the reclamation step must also be disposed
of as hazardous waste.
Even though acetone is classified as a non-volatile
organic compound (VOC), its hazardous qualities are still
strong incentives for FRP shops to implement alternatives.
These qualities include fire hazards associated with elevated
concentrations of vapors and waste management of the spent
hazardous solvent. Acetone substitutes can be used to reduce
volatile emissions. These substitutes are grouped into two
general categories including higher-boiling solvents and aqueous
cleaners.
Higher-boiling Solvents
These solvents work the same way as acetone, by dissolving
the resin. When using higher-boiling substitutes the liquid
film remaining on the part may be removed with a towel or
by some other means, as these solvents do not evaporate as
readily.
Higher-boiling solvents can be substituted
for acetone in many applications. However, their effectiveness
needs to be verified for each cleaning situation. Carefully
review the Material Safety Data Sheet (MSDS) to note any potential
safety or worker exposure hazards. Protective equipment such
as splash goggles and gloves may be necessary.
Aqueous Cleaners
Aqueous cleaners rely on mechanical action, such as brushing,
to clean resin from contaminated surfaces. The mechanical
action separates resin from the part surface and the resin
droplets are wetted by the aqueous cleaner. The coated resin
settles to the bottom of the cleaning tank. A towel or a stream
of air can then be used to dry the tool prior to reuse.
Although aqueous cleaners eliminate volatile
emissions, they create two other waste streams including the
spent aqueous solution and the under-cured resin material
collected in the cleaning tank.
Information from the MSDS for some aqueous
cleaners suggest that the spent liquid solution can be disposed
of by sewering. However, prior to disposal, be sure to obtain
approval from your local sewage treatment facility and comply
with all local, state and federal regulations.
Both higher-boiling solvents and aqueous
cleaners are effective substitutes, but special attention
is demanded when educating employees about new cleaning procedures.
Lack of training usually results in poor cleaning, and employees
lack of acceptance causes implementation to fail.
Managing Small Amounts
of Waste Resin or Gelcoat
Small batches of uncured resin or gelcoat can be disposed
of as nonhazardous solid waste if they are hardened by adding
an appropriate amount of catalyst. Refer to the Minnesota
Pollution Control Agencys Best Management Practices
for Treating Waste Polyester-Resin and Gelcoat
fact sheet for the requirements and proper procedures.
Additional
Sources of Information
The following publications and
Web sites provide further information on waste reduction
in the fiberglass fabrication industry: |
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Composites Fabricators
Association Open-Molded Styrene Emissions Test Project:
Phase IBaseline Study for Hand Lay-up, Gel Coating,
Spray-up, including Optimization Study, Composites
Fabricators Association, 1996. |
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Hillis, David. Establishing
Waste Reduction Benchmarks and Good Manufacturing Practices
for Open-Mold Laminating, North Carolina Division
of Pollution Prevention and Environmental Assistance,
1997. |
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Hillis, David and David,
Darryl. Waste Reduction Strategies for Fiberglass Fabricators,
East Carolina University, 1995. |
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Composites
Fabricators Association. |
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Pacific
Northwest Pollution Prevention Resource Center. |
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Composite
Materials Technology Center (COMTEC). |
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Coating
Applications Research Laboratory
(CARL). |
References |
1. |
Unified
Emission Factors for Open Molding of Composites, Composites
Fabricators Association, April 7, 1999. |
2. |
Briedenbach, D. and Dotson,
E. "The Practical Use of Styrene Suppressants and
Testing with the CFAs 'Vapor Suppressant Effectiveness
Test,'" Composites Fabrication. November/December
2000, p. 28. |
3. |
Noonan, J.R. and Hall,
S.J. New Gel-Coat Application Technology Emission Study,
Coating Applications Research Laboratory (CARL), Clean
Manufacturing Technology and Safe Materials Institute,
Purdue University, November 22, 2000. |
4. |
GENMAR
Governors Award Summary, Minnesota Office of
Environmental Assistance, September 2000. |
5. |
Lacovara, B. "Controlled
Spraying: New Techniques for EfficiencyWith No Downsides,"
Composites Fabrication. March 1998, p. 8. |
6. |
Schwamberger, R. "How
Robots are Used in the Composites Industry," Composites
Fabrication. July 2000, p. 28. |
7. |
Best Management Practices
for Treating Waste Polyester-Resin and Gelcoat, Hazardous
Waste Division Fact Sheet #4.50, Minnesota Pollution
Control Agency, April 1997. |
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