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Finishing E-Books
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ABC's of Finishing - ITW DeVilbiss
Basic to moderate finishing training. |
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Spray Gun Troubleshooting
How does your spray gun shape up? Find out why your spray gun may
not be performing correclty. |
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Selecting Filtration - Chemco
A great guide for filter selection criteria |
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Selecting Powder Filtration - Chemco
Learn how to define and select the right cartridge filtration for
your powder spray application. |
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Graco Series Of Training Modules
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Understanding Compressed Air
Air Spray Technology
Atomization
Electrostatic Finishing Basics
Fluid Handling Basics
Fluid Characteristics
Moving Paints and Coating
Moving Thick Fluids
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| Finishing Safety |
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| Pressure Loss Calculator |
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Technical Data Reference
Excellent reference for system design |
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Understanding the Finishing Process
Reduce Polutants through increased knowledge.
Many products require some type of coating such as paint, lacquer,
or varnish. Because the use of coatings is widespread, there is great
potential for environmental benefit and for cost savings in pollution
prevention techniques that are part of a coating application process.
Source reduction and recycling techniques can reduce hazardous and
solid waste generation and reduce air emissions, not to mention reduce
use
of raw materials and conserve water. An assessment of a coating operation
may reveal ways to reduce waste generation through pollution prevention.
Start with Surface Preparation
Many products require a preparation step prior to painting. This step
is commonly called pretreatment for new products, and paint stripping
for products that need to be reworked.
Pretreatment
For waste reduction in pretreatment of new parts, the first step is assessing
cleanliness of the parts: to what degree are the surfaces contaminated
with substances such as oil from machining, dirt from the manufacturing
environment, and finger oil from shop personnel? An important part
of the assessment is to determine the sources of contamination.
The next step is to determine the cleanliness level or standard needed
to satisfy the pretreatment process. Once the contamination sources are
identified and cleanliness standards are set, determine whether some
or all contamination sources can be eliminated. For example, it may be
possible to eliminate finger oil contamination through the use of gloves
in areas of parts handling. Gloves can be made of lint free material,
or lint can be removed with a dry cloth.
If contamination cannot be reduced enough through process changes, cleaning
methods must be assessed.
Ozone layer-depleting solvents have been commonly used as cleaning agents.
But environmental concerns and regulations affecting production and use
of these solvents have caused many companies to reassess their use of
this type of solvent as a cleaning agent.
There is seldom a "drop-in" replacement for a halogenated
organic solvent in a cleaning operation. Substitutes may include: non-
halogenated solvents; aqueous cleaners, such as alkaline or acid cleaners,
or detergent/water solutions; and abrasive cleaning systems. In general,
like removes like. Ionic contaminants (finger prints, flux, etc.) can
best be removed with ionic solvents, such as water or alcohol. Contaminants
that are organic in nature (oils) can be best removed either with organic
solvents or with water that has had surfactants added to make the oil
and water miscible. Important factors in the design of the new cleaning
system include the nature of the contamination, the substrate to be cleaned,
and the degree of cleanliness required. The best alternative method can
be determined only through testing.
Another pretreatment method often used in the surface preparation of
metal parts is phosphatizing. The primary waste reduction option for
phosphatizing is reduced water use. The water added to maintain the solution
in the phosphatizing bath can be reduced by analyzing and controlling
each solution s temperature, chemical concentration, and pH level in
each step, and by recirculating solution or rinse water from one bath
to others where possible. An added benefit is the potential for reduced
chemical use.
Paint Removal
When repainting a part, the old paint often must be removed prior to
application of the new paint coat. The waste reduction assessment should
start by examining what causes the need for repainting: inadequate
initial part preparation; defects in coating application; equipment
problems; or coating damage due to improper handling.
While no process is perfect, reducing the need for repainting has a
direct effect on the volume of waste generated from paint removal. Once
the need for paint stripping has been reduced to a minimum, alternate
paint stripping approaches can be considered.
Key concerns are the type and volume of waste produced. Chemical stripping
commonly has been used in a number of applications, but alternate methods
that are less toxic and less costly are available. For example, a barrel
reconditioning operation was able to replace chemical stripping with
mechanical stripping using metal and nylon brushes.
Paint-stripping technologies that are alternatives to chemicals include:
abrasive blasting with a variety of materials; mechanical removal using
scrapers, wire brushes and sand paper; pyrolysis (vaporization of the
paint coating in a furnace or molten salt bath); cryogenics ("freezing" the
paint off); and extremely high-pressure water or air.
Key factors that must be considered when selecting a paint-stripping
method include: potential for cross-media transfer; the characteristics
of the substrate to be stripped; the type of paint to be removed; and
the volume and type of waste produced. Waste type and volume can have
a major impact on cost-benefits associated with a change. Often, a combination
of removed paint and chemical stripper requires disposal as hazardous
waste.
Paint and Painting Equipment
Once parts are ready to be painted, the type of coating material and
application method selected have an impact on transfer efficiency.
Transfer efficiency is the amount of paint applied to the object being
painted, divided by the amount of paint used. High transfer rates offer
financial incentives by reducing the amount of paint wasted while minimizing
solid, liquid, and air emissions. Simply stated, transfer efficiency
measures how much paint makes it from the paint can onto the surface
being painted.
In spray-painting applications, liquid paint is converted to an atomized
spray in order to coat the object being painted. Differences in spray-
painting equipment are based on how the equipment atomizes paint. The
more highly atomized the paint, the more likely transfer efficiency is
to decrease. Highly atomized paint spray can more readily drift away
from the painting surface due to forces such as air currents and gravity.
To achieve the best transfer efficiency, it is advisable to study the
application equipment available and actually evaluate equipment performance
using each coating material considered acceptable for your application.
Because each application equipment combination has its own characteristics,
the advantages and disadvantages must be weighed against the coating
specifications set for a particular product.
The viscosity of the paint may need adjustment before it can be sprayed.
This is accomplished by reduction with organic solvents, or with water
for certain water-based coatings. Using solvents for reduction requires
the purchase of additional materials and increases air emissions. An
alternative method of reducing the viscosity is to use heat. Benefits
from the purchase of paint heaters include lower solvent usage, lower
solvent emissions, more consistent viscosities, and faster curing rates.
Spray Application Equipment
Conventional Spray - This technology, in use for over 40 years, uses
air at high pressure (40 - 70 pounds per square inch [psi]) to atomize
a liquefied stream of paint. The high-energy air stream that is mixed
with the paint causes atomization that is generally very fine and easily
applied. This yields very good finishes with high-quality visual characteristics.
A disadvantage is that along with a high degree of atomization comes
a spray that is very fine and highly susceptible to overspray, resulting
in more paint waste and less transfer efficiency. The solvent in the
paint is also highly atomized along with the paint solids, meaning that
volatile organic compound (VOC) emissions from the solvent in paint are
increased.
High-Volume/Low-Pressure (HVLP) - As the name suggests, a high volume
of air at low pressure is used to atomize paint. The defined air-pressure
limit for HVLP is 10 psi at the center of the air cap on the spray gun.
It is this reduced gun spray energy level that reduces overspray and
improves transfer efficiency. Generally, fluid delivery rates up to 10
ounces per minute with low viscosity paint will work best with the HVLP
gun. However, continued development is underway to accomplish faster
delivery rates to accommodate higher production. At higher fluid- delivery
rates and with heavier materials, HVLP may not atomize well enough to
achieve an acceptable finish.
Airless - This is a method of atomizing paint without the use of compressed
air. The paint is pumped at high pressure through a small opening at
the spray tip to achieve atomization. Adjustments in airless spraying
are made by adjusting the viscosity or the system pressure. This method
has higher transfer efficiencies than conventional spray. Many high-viscosity
coatings can be applied without costly solvent thinning. Also, this method
allows for rapid application of a heavy paint coat, which is useful for
keeping up with a fast-moving painting line.
Air-Assisted - This is a spraying system that helps or "assists" airless
systems by using supplemental air jets to guide the paint spray and boost
the level of atomization. Air-assisted airless technology combines the
best characteristics of both air and airless spray. Benefits include
substantial material savings and reduced overspray when compared to conventional
air spray, and improved transfer efficiency and finishing appearance
when compared to airless technology. The ability to reduce the fluid
pressure from airless is the primary factor in the increased finish quality.
Operator technique also is enhanced as the application rate is reduced
and the operator can more easily coat the product uniformly.
Electrostatics - With this method, the paint and the part are given
opposite electrical charges. The result is that transfer efficiency is
increased because the paint is drawn to the part by an electric field.
As a result, paint spray is less susceptible to drafts and air currents
that increase overspray. Even water-based paints can be applied with
a high-voltage electrostatic charge in some cases.
Rotary Atomization - This application system atomizes paint by dropping
a stream of liquid on a disk or bell-shaped object spinning at high speed.
Rotary atomizers utilize electrostatics to attract paint to the part.
Rotary atomization is useful for high-viscosity paints. This process
can create a spray without use of thinner and tends to have high transfer
efficiency. However, the equipment needed for this type of application
is very specialized and usually requires a major conversion of a painting
line.
Spray Booths - Two basic types of enclosures are used in most painting
applications: dry booths and wet booths. The key difference is that a
dry booth depends on a filter of paper, fiberglass, Styrofoam , or metal
to collect overspray, while the wet booth uses water with chemical additives.
The type of booth selected can affect the volume and type of paint waste
generated. Decisions made about this equipment should be made based on
the type and volume of painting done and the volume of waste generated.
Generally, small-volume painting operations will find the lower purchase
cost of a dry filter booth will meet their requirements. One disadvantage
in the use of a dry-filter booth is in the disposal of the waste. Typically
the majority of this waste is the filter media itself which has been
contaminated by a relatively small amount of paint. Reusable filters
may decrease waste volume and reduce disposal cost. In some applications,
overspray can be collected for reuse.
If overall painting volume can justify the investment, a wet booth may
work to your advantage. This type of booth eliminates disposal of filter
media and allows waste to be reduced in weight and volume. This is achieved
by separating the paint from the water through settling, drying, or using
a centrifuge or cyclone.
Coating Types
Organic Solvent-Based This is the traditional type of painting material,
typically containing about 40 percent solids with a relatively high
organic-solvent content. While this coating material is one of the
most versatile, its low solid content and high percentage of solvent
carrier can cause it to have low overall (solids) transfer efficiency.
To get the required coverage, more material must be sprayed compared
to materials with higher solids content and lower VOC emissions.
High-Solids - This paint type has a higher percentage of paint solids
and a lower percentage of solvent carrier. Overall transfer efficiency
tends to be better than traditional solvent-based paint. The increased
solids content means that fewer applications are needed to get the required
film thickness. Air emissions from the solvent are generally lower due
to reduced organic solvent content. However, a paint heater may be required
to reduce viscosity and the film thickness is more difficult to control.
Water-Based - These paint types typically have a high solids content,
utilize water as the solvent, and have very low or no organic-solvent
content. Advantages of these paint types include reduced VOC emissions,
reduced fire hazard, minimized or eliminated hazardous waste disposal,
and easy cleanup. However, using a water-based coating may require stainless
steel components in the preparation and delivery areas, a cleaner surface,
longer drying times, increased oven temperatures, and a temperature-controlled
paint storage area. The switch to water-based materials must be done
carefully. Water-based coating technology is the fastest changing in
the market today.
Catalyzed or Two-Component - These coatings are created by mixing two
low-viscosity liquids just before entering the application system. One
liquid contains reactive resins, and the other contains a catalyst that
promotes polymerization of the resins. These coatings eliminate or reduce
solvents and cure at low temperatures.
However, it is important to remember that catalysts and paint components
may be hazardous themselves and create a different set of emission and
exposure problems than those of organic solvents. Catalyzed painting
also means that more material may be used if strict attention is not
paid to the pot life.
Powder Coating - These coatings use 100 percent resin in dry, powdered
form which must cure in an oven. Powder-coating materials can provide
a high-quality, durable, corrosion-resistant coating. There are little
to no VOC emissions, hazardous overspray wastes, or waste- water sludges.
With powder coating it is also possible to collect the dry coating material
that doesn t stick to the part and reuse it. Reuse allows powder coaters
to achieve very high transfer efficiencies.
Powder coating requires specialized application equipment using electrostatic
charges to apply the material. Its use also means that the substrate
must be able to tolerate the curing temperature of the oven (typically
300 - 450o F). However, advancements in powder coating formulations are
occurring at a rapid pace, and new coating powders are increasingly becoming
available to meet special manufacturing needs.
Radiation Cured - Ultraviolet (UV), Electron Beam (EB), and Infrared
(IR) coatings use electromagnetic radiation to cure. These coatings typically
have lower VOC content than conventional coatings, require smaller ovens,
and allow for increased production rates due to shorter curing period.
The shape of the part will effect the curing; flat surfaces are easiest
to cure. Capital investments are usually higher than conventional ovens
and the cost of the raw material coating is higher.
This partial listing of equipment and coating options is only a summary
of the technology available. Ohio EPA's Office of Pollution Prevention
(OPP) can provide reference materials on these topics. Valuable information
and hands-on training also can be obtained from your equipment vendors
and suppliers.
Operator Techniques
The techniques spray painters use during application have a definite
effect on transfer efficiency and have waste reduction potential. The
fundamentals of good spray technique consist of: the proper overlap
of the spray pattern; the proper gun speed; the proper distance of
the gun from the part; holding the gun perpendicular to the surface
of the part; and triggering the gun at the beginning and end of each
stroke.
The proper overlap of the spray patterns will be determined by the coating.
Proper overlap may range from 50 percent to 80 percent. Greater overlap
may result in wasted strokes, and less overlap may result in streaks.
Since the flow of coating from the gun is consistent, the speed of the
gun as it is moved across the part should be consistent also. Steady
gun speed will help obtain a uniform thickness of coating. A gun speed
higher than manufacturer specifications can distort the spray pattern
and not permit the maximum amount of material to reach the surface.
The distance of the gun from the part must be consistent, since, again,
the flow of material from the gun is consistent. Generally, this will
be six to eight inches for non-electrostatic systems. Spray losses increase
with the distance as does solvent loss. This solvent loss is often corrected
by the addition of more solvent. This does not correct the spray loss,
and overspray still ends up in the spray booth.
Except for special conditions, the gun should be held perpendicular
to the surface of the part. Arcing the gun for hard to reach areas wastes
material by applying an uneven coat. This also may result in streaks.
These areas should be compensated for by changing the positioning of
the gun or of the operator.
If the trigger of the gun is not released at the end of a stroke, the
material continues to flow and, when the gun changes direction, the momentary
stopping of the gun results in an accumulation of coating material. To
avoid this piling, the operator may spray past the edge of the surface,
spraying material into the spray booth and wasting coating.
All manufacturer specifications should be checked to ensure that operators
are using the proper technique for their equipment. Operator training
and experience will provide operators with knowledge of the various painting
techniques needed to paint parts of different configurations. Different
techniques are helpful when painting inside corners, outside corners,
slender parts, round parts, flat parts, large parts, or small parts.
A training program for spray operators should take advantage of their
pride in the finish they produce. The program should be presented as
a means for them to obtain a higher quality of finish. The various fundamentals
should not only be taught, but also explained, so operators understand
the advantages of good technique.
Standard operating techniques will not be fully successful if other
problems exist, such as the room temperature changing throughout the
day (which changes the viscosity of the paint), or if equipment needs
repair. Operators cannot be expected to compensate for broken gauges,
worn fluid tips, or other equipment problems.
Whenever adjusting the spray technique of operators, it is important
to note that over a period of time the coating and the selection or use
of equipment may have been made to conform to the present incorrect technique.
Equipment settings and materials may need to be changed to conform to
the improved technique (DeVilbiss).
Equipment Cleaning
When a painting process is completed, a color change is needed, or maintenance
is required during regular operation, equipment cleaning is required.
Equipment cleaning offers opportunities for waste reduction and for
reductions in air emissions.
When assessing the cleaning process, all the typical cleaning tasks
should be reviewed to learn whether cleaning is necessary. While it is
assumed that spray guns, tips and lines must be cleaned for reuse, cleaning
some low cost items may not be advisable. Costs from cleaning solvent
purchases, solvent waste disposal and solvent emissions could be higher
than simply replacing the item being cleaned. However, the cost of proper
disposal must be taken into account.
Next, the ways in which cleaning solvents are handled should be reviewed.
All solvents should be in covered containers when not in use. Leaving
solvents in the open air creates unnecessary solvent waste and VOC emissions.
In addition, a standard should be set to assure that used solvent is
disposed of or recycled only when it loses its cleaning effectiveness,
not just because it looks dirty.
For equipment that requires cleaning, methods that minimize solvent
use and reduce evaporation should be implemented wherever practical.
Using a gun washer to clean spray guns is one example. A gun washer is
a piece of equipment similar to a dishwasher. It is designed to hold
a number of spray guns and related equipment and cleans by circulating
solvent inside a closed chamber. The result is rapid cleaning and extended
solvent cleaning life while reducing solvent waste and the emissions
from evaporation. Line cleaning is another area where use of special
equipment can decrease cleaning time, improve efficiency of solvent use,
and decrease waste. One method used to improve line cleaning efficiency
is to introduce turbulence into the solvent going through the line during
cleaning. Equipment that forces alternating pulses of solvent and compressed
air is one way to accomplish this. Payback on this equipment can come
from increased production output through more rapid color changes as
well as from material savings through decreased solvent use.
Solvent Reuse Alternatives
On-site recycling of used solvent is another way to reduce waste and
save money. First, savings come from reducing the amount of solvent
purchased. Second, savings come from reduced disposal cost by reducing
the volume of spent solvent that must be sent off-site. Three common
methods of solvent recycling are settling, filtering, and distilling.
Settling is putting used solvent in a container and letting the particulate
matter settle out. The container should be designed to allow removal
of solvent without shaking up the sludge which has settled out. Filtering
equipment, which removes the particulate matter from solvents, is also
available. Distillation is an attractive option for many organic solvent
users. Equipment is available in a variety of sizes. For more information,
request OPP's fact sheets "On-site Solvent Recycling Equipment" and "Legal
Considerations for On-site Solvent Recycling."
Alternative Solvents
Due to the increased need to reduce VOC emissions, alternative cleaning
solvents are being used. They include dibasic esters (DBE) and dimethyl
sulfoxide (DMSO). Although toxicology information specific to these
chemicals is relatively limited at this time, it is believed that the
relative safety of similar chemicals means that they might be viable
alternatives to organic solvents in certain applications.
References and Sources of Information
Browner, Carol. 1994. The Common Sense Initiative: A New Generation of
Environmental Protection. Presented at the July 20, 1994 Center for
National Policy Newsmaker Luncheon. U.S. EPA, Washington, DC.
DeVilbiss Educational Services. The Efficient Utilization of Material
in the Finishing Room. DeVilbiss. Maumee, Ohio. Material used with permission.
The Minnesota Technical Assistance Program. 1993. Waste Reduction Alternatives
for Spray Painting and Coating. The Minnesota Technical Assistance Program,
Minneapolis, Minnesota. Material reprinted with permission.
The Powder Coating Institute. 1994. Powder Coatings: Technology of the
Future, Here Today. The Powder Coating Institute, Alexandria, Virginia.
U.S. EPA. 1990. Guides to Pollution Prevention - The Fabricated Metal
Products Industry. EPA/625/7-90/006. U.S. EPA, Washington, DC.
Wolf, Katy. 1994. The Truths and Myths about Water-Based Cleaning: A
Systems Approach to Choosing the Best Alternatives. Pollution Prevention
Review. Vol. 4, No. 2, Spring, 1994.