SEPA
                         United States
                         Environmental Protection
                         Agency
                         Research and Development
                                    Risk Reduction
                                    Engineering Laboratory
                                    Cincinnati, OH 45268
                                    EPA/600/S-92/029   Sept. 1992
ENVIRONMENTAL
RESEARCH   BRIEF
                          Waste Minimization Assessment for a
                   Manufacturer of Cutting and Welding  Equipment

                       Harry W. Edwards", Michael F. Kostrzewa*. and Gwen P. Looby"
Abstract
The U.S. Environmental Protection Agency (EPA) has funded
a pilot project to assist small- and medium-size manufacturers
who want to minimize their generation of waste but who lack
the expertise to do so. In an effort to assist these manufactur-
ers Waste Minimization Assessment Centers (WMACs) were
established at selected universities and procedures were
adapted from the  EPA Waste Minimization Opportunity  As-
sessment Manual (EPA/625/7-88/003, July 1988). The WMAC
team at Colorado State University performed an assessment at
a plant that produces custom-built cutting and welding equip-
ment. Components are fabricated from steel and other  raw
materials that are  cleaned,  machined, welded, and painted.
Machines are then assembled, tested, and calibrated. The
hazardous  wastes  generated by the  plant include tramp oil,
spent cutting fluid, spent lacquer thinner, and chromium-con-
taminated paint  dust and filters. The team's report, detailing
findings  and recommendations, indicated that the plant could
achieve  the greatest dollar  savings by replacing chromium-
containing solvent-based paints with chromium-free water-based
paints.

This Research Brief was developed by the principal investiga-
tor and EPA's Risk Reduction Engineering Laboratory, Cincin-
nati, OH, to announce  key  findings of  an ongoing research
project that is fully documented in a separate report of  the
same title that is available from University City Science Center.


Introduction
The amount of waste generated by industrial plants has become
an increasingly costly problem for manufacturers and an addi-
' Colorado State University, Department of Mechanical Engineering
" University City Science Center, Philadelphia, PA
                        tional stress on the environment. The primary solution to the
                        problem of waste is to reduce or eliminate it at its source.

                        University City Science Center (Philadelphia, PA) has begun a
                        pilot project to assist small- and medium-size manufacturers
                        who want to minimize their formation of waste but who lack the
                        inhouse expertise to do so. Under agreement with EPA's Risk
                        Reduction  Engineering Laboratory, the Science Center has
                        established three  WMACs. This assessment was done by
                        engineering faculty and students at Colorado State University's
                        (Fort Collins) WMAC. The assessment teams have considerable
                        direct experience  with process operations in manufacturing
                        plants  and also have the knowledge and skills  needed to
                        minimize waste generation.

                        The waste minimization assessments are done for  small- and
                        medium-size manufacturers at  no out-of-pocket cost  to  the
                        client.  To qualify for the assessment, each client must fall
                        within Standard Industrial Classification Code 20-39,  have gross
                        annual sales not exceeding $75 million, employ no more than
                        500 persons, and lack inhouse expertise in waste minimization.

                        The potential benefits of the pilot project include minimization
                        of the  amount of waste generated by manufacturers and re-
                        duction of waste treatment and disposal costs for participating
                        plants, in addition, the project provides valuable experience for
                        graduate and undergraduate students who participate  in  the
                        program and a cleaner environment without more regulations
                        and higher costs for manufacturers.


                        Methodology of Assessments
                        The waste minimization assessments require several site visits
                        to each client served. In general, the WMACs folbw the pro-
                        cedures outlined in the EPA Waste Minimization Opportunity
                        Assessment Manual (EPA/625/7-88/003, July 1988). The
                                                                              Printed on Recycled Paper

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WMAC staff  locate the sources of waste in the plant  and
identify the current disposal or treatment methods and their
associated costs. They then identify and analyze a variety of
ways to reduce or eliminate the waste. Specific measures to
achieve that goal are recommended and the essential supporting
technological and economic information is developed. Finally,
a  confidential report that  details  the  WMAC's  findings  and
recommendations (including cost savings, implementation costs,
and payback times) is prepared for each client.


Plant Background
The plant manufactures custom-built welding equipment  and
cutting machines. It operates approximately 4,500 hr/yr to  pro-
duce  more than 80 machines annually.


Manufacturing Process
This plant produces welding equipment and cutting  machines
that are custom-built to meet clients' requirements. The major
raw material  is steel; however, iron, aluminum,  brass, zinc-
plated steel, and phenolic materials are also used.

Prior to fabrication, the metals are cleaned using a spray wand
to remove residual rust-preventing oil. A flame cutter is then
used  to cut  the  metal to workable dimensions.  The material
undergoes machining with drills, lathes, and cutting and milling
machines. The parts  are  then mechanically cleaned using
grinders and sanders. Welding  is performed as necessary.

Components to be painted are first treated with alkaline cleaner
and phosphate solution in a series of dip tanks. Solvent-based
acrylic lacquers and enamels are applied using  spray guns in
the paint booth. Logos are  applied using silk-screening.

The various components  are  then  assembled,  tested,  and
calibrated. An  abbreviated  process flow diagram  that also de-
scribes waste generation is shown in Figure 1.


Existing Waste Management Practices
This plant has already implemented the following techniques to
manage and minimize its wastes.

  • A portable oil skimmer is used to remove tramp oil from
    the cutting fluid in the sumps of the computer numerically-
    controlled  (CNC)  machines. The  decreased amount of
    tramp oil in the sumps  has  increased the life of the cutting
    fluid.
  • A belt skimmer and filter are used to remove tramp oil  and
    paniculate matter from the cutting fluid drained from  the
    CNC machines so that the fluid can  be reused in  the
    manual machining equipment.
  • The phosphating dip line used prior to painting was in-
    stalled to reduce the use of lacquer thinner for cleaning
    and degreasing.
  • Electronic  assemblies  are cleaned with a terpene hydro-
    carbon cleaner instead of perchloroethylene.
   •  High-volume low-pressure paint guns are used in order to
     reduce overspray and conserve paint.
   •  Water-based paints are being evaluated on a trial basis as
     a replacement for the solvent-based paints currently used.


 Waste Minimization Opportunities
 The type of waste currently generated by the plant, the  source
 of the waste, the quantity of the waste, and the annual treat-
 ment and disposal  costs are given in Table 1.

 Table 2 shows the opportunities for waste minimization that the
 WMAC  team recommended for the  plant. The type of  waste,
 the minimization opportunity, the  possible waste reduction and
 associated savings, and the implementation cost along with the
 payback times are given  in the table. The quantities of waste
 currently generated by the plant and possible waste  reduction
 depend on the production level of the plant. All values  should
 be considered in that context.

 It should be noted that the economic savings of the minimization
 opportunity, in most cases, results from the need for less raw
 material and from reduced present and future costs associated
 with waste treatment and disposal. Other savings not quantifi-
 able  by this  study  include a wide  variety of  possible future
 costs related to changing emissions standards, liability, and
 employee health. It should also be noted that the savings given
 for each opportunity  reflect  the savings  achievable  when
 implementing each waste minimization opportunity independently
 and  do  not reflect duplication of savings that may result when
 the opportunities are implemented in a package.


 Additional Recommendations
 In addition to the opportunities recommended and analyzed by
 the WMAC team, additional measures were considered.  These
 measures were not completely analyzed because of insufficient
 data, minimal savings, implementation difficulty, or a projected
 lengthy  payback. Since one or more of these approaches to
 waste reduction may, however, increase in attractiveness with
 changing conditions  in the plant, they were brought  to the
 plant's attention for future consideration.

  • Test the waste cutting fluid  from  the  CNC machines to
    determine if  the lead  and benzene concentrations are low
    enough that the waste could be  shipped  to  a disposal
    facility for nonhazardous waste.
  • Evaluate the need for the application of rust-preventive oil
    to the raw material. It is  possible that the rust-preventive
    oil is unnecessary thereby reducing the need for cleaning.
  • Segregate the scrap metal by type to increase the amount
    of revenue received.

This research brief  summarizes a part of the work done under
Cooperative Agreement No. CR-814903 by the University City
Science Center under the  sponsorship of the U.S. Environmen-
tal Protection Agency. The EPA Project Officer was Emma Lou
George.

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                                Steel, Iron,
                                Zinc-Plated Steel,
                                Aluminum, Brass,
                                Phenolic Materials
                               Cleaning
                                - Water Spray
           Wastewater to Sand/Oil
           Interceptor and Sewered
                              Machining
                               - Flame-Cutting
                               - Drilling, Cutting
                               - Milling
            ^  Tramp Oil and Spent
               Cutting Fluid Incinerated
           \Offsite
                                                           (Waste Oils foN
                                                           \   Reclaimer      J
                            Mechanical Cleaning
                            - Debarring & Polishing
                Slag and Grinder
                Dust Accumulating
                Onsite
                            Painting
                            - Pro- Treatment
                            - Spray-Painting
                            - Silkscreen Painting
                                                            Waste Aqueous
                                                            Cleaner Accumulating
                                                            Onsite
                               Final Assembly
                               - Testing
                               - Calibration
             Paint Dust and Filters.
             Waste Thinner, and
             Equipment Cleaner
             Incinerated Off site
Wastewater to Sand/Oil
Interceptor and Sewered
                                                                      Slag Accumulating Onsite
                             Jnsitej
Figure 1.  Abbreviated process flow diagram.

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Table 1.  Summary of Current Waste Generation
Waste Generated
 Source of Waste
Annual Quantity
   Generated
  Annual Waste
Management Cost
Wastewater





Wastewater




Tramp oil



Spent cutting fluid



Miscellaneous waste oil




Slag and grinder dust


Scrap metal


Wastewater



Waste aqueous degreasers




Spent lacquer thinner




Equipment cleaning solvent
Chromium-contaminated
paint dust and filters


Wastewater
Slag
Spray wand phosphating/cleaning.
Wastewater from the removal of rust-
preventing oil from metal prior to
fabrication is drained to a sand and
oil interceptor and then sewered as
industrial wastewater.
Flame cutting.
Cooling water that is used to prevent
metal warping during flame cutting
is drained to a sand and oil interceptor
and then sewered as industrial wastewater.
Machining.
Tramp oil from cutting fluid is shipped
off site for incineration at a hazardous
waste disposal facility.
Machining.
Cutting fluid that cannot be reused is
shipped offsite for incineration at a
hazardous waste disposal facility.
Various plant equipment.
Waste motor oil and lubricating oil from
forklifts and other plant equipment is
shipped offsite for reclamation as industrial
boiler fuel.
Machining.
Slag resulting from flame cutting and
grinding dust are accumulating onsite.
Machining
Scrap metal generated by sawing and
machining operations is sold to a recyder.
Paint line pretreating.
Water used for pretreating prior to painting
is drained to a sand and oil interceptor and
then sewered as industrial wastewater.
Paint line pretreating.
Waste aqueous cleaners used in small
volumes are stored onsite pending
analysis and determination of a proper
disposal method.
Painting.
Lacquer thinner used to degrease parts
prior to painting is shipped offsite for
incineration at a hazardous waste disposal
facility.
Painting.
Solvent used to clean paint guns and other
painting equipment is shipped off site for
incineration at a hazardous waste disposal
facility. (This solvent is no longer used; it
has been replaced by the lacquer thinner.)
Painting.
Paint fitters that trap overspray and paint
dust are shipped offsite for incineration at
a hazardous waste disposal facility.
Assembly and testing.
Cooling water used in flame cutting testing
is drained to a sand and oil interceptor and
then sewered as industrial wastewater.
Assembly and testing.
Slag resulting from flame cutting testing is
accumulating onsite.
   210,000 gal





   437,500 gal




       495 gal



       420 gal



       400 gal




  Not available


  Not available


     23,000 gal



  Not available




       810 gal




        95gal





       1,390lb



      3,180 gal



  Not available
      1500'





      f,040'




       2,310



        1960



          80




          0*


Not available.


         60'



          0*




      4,430'




       5/0'





       5,670



         10'



          0*
'Includes cost of raw material.
'Accumulating onsite; no waste management costs incurred.

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Table 2.  Summary of Recommended Waste Minimization Opportunities
Waste Generated
Chromium-contaminated
paint dust and filters
Spent lacquer thinner
Minimization Opportunity
Replace chromium-containing
solvent-based paints with
chromium-free water-based paints.
Paint dust and filters can then be
disposed of in the municipal
landfill without an increase in
trash hauling fees. The purchase
of lacquer thinner and the
subsequent disposal of spent
thinner will be reduced.
Annual Waste Reduction Net Implementation
Quantity Percent Annual Savings Costs
1,390lb 100 $4,1 80 ' $1,000
40 gal 5
Payback
Years
0.2
Spent lacquer thinner
Spent cutting fluid
Spent cutting fluid
Spent cutting fluid
Install a distillation unit to recover      610 gal          75
lacquer thinner for reuse. The
amount of spent thinner shipped
off site for disposal and the
amount of lacquer thinner
purchased will be reduced.

Acid treat the cutting fluid waste       240 gal          57
from the CNC machines to effect
a separation of organic and aqueous
phases. Discharge the aqueous phase
to the industrial sewer and dispose
of the organic phase at a hazardous
waste disposal facility.

Heat the cutting fluid waste from      240 gal          57
the CNC machines to evaporate
the aqueous phase and reduce
the volume of waste sent to the
offsite hazardous waste disposal
facility.

Replace the  cutting fluid used in       150 gal          36
the track mill with a vegetable oil-
based spray coolant that is bio-
degradable and completely
consumed during cutting.
2,300**
7,060
3.1
 1,100s
1,000
0.9
 1,070'
2,800
2.6
   7703
1,210
                                     1.6
1 Total waste management cost savings have been reduced by increased raw material costs.
'Total waste management cost savings have been reduced by the operating cost of the proposed system.
'Includes savings on raw materials.
                                                                              &U.S. GOVERNMENT PRINTING OFFICE: t*94 • 5SO-O67/80I55

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