f,EPA
                         United States
                         Environmental Protection
                         Agency
                                    Risk Reduction
                                    Engineering Laboratory
                                    Cincinnati, OH 45268
                         Research and Development
                                    EPA/600/S-92/064   October 1992
ENVIRONMENTAL
RESEARCH   BRIEF
                     Waste Reduction Activities and Options for a
                          Manufacturer of Orthopedic Implants

                                   Alan Ulbrecht and Daniel J. Watts*
Abstract
The U.S. Environmental Protection Agency (EPA) funded a
project with the New Jersey  Department of  Environmental
Protection and Energy (NJDEPE) to assist in conducting waste
minimization assessments at 30 small- to medium-sized busi-
nesses in the state of New Jersey. One of the sites selected
was a facility that manufactures orthopedic implants for use by
the health care industry. The parts are produced in a molding
operation using stainless steel or cobalt chromium alloy. Com-
puter-controlled cutting is used to produce the bearings for the
implants according to precise specifications. A site visit was
made in 1990 during which several opportunities for waste
minimization were identified. Options identified include onsite
distillation and reuse of solvent, alternative degreasing tech-
niques, and reuse of metal cutting fluids. Implementation of the
identified waste minimization opportunities was not part of the
program. Percent waste reduction, net annual savings, imple-
mentation costs and payback periods were estimated.

This Research Brief was developed by the Principal Investiga-
tors and EPA's Risk Reduction Engineering Laboratory in Cin-
cinnati, OH, to announce key findings of this completed as-
sessment.


Introduction
The environmental issues facing industry today have expanded
considerably  beyond traditional concerns. Wastewater, air
emissions, potential soil and groundwater contamination, solid
waste disposal, and employee health and safety have become
increasingly important concerns. The  management and dis-
posal of hazardous substances, including both process-related
wastes and residues from waste treatment, receive significant
attention because of regulatbn and economics.
* New Jersey Institute of Technology, Newark, NJ 07102
                        As environmental issues have become more complex, the
                        strategies for waste management and control have become
                        more systematic and integrated. The positive role of waste
                        minimization and pollution prevention within industrial operations
                        at each stage of product life is recognized throughout the
                        world. An ideal goal is to manufacture products while generat-
                        ing the least amount of waste possible.

                        The Hazardous Waste  Advisement Program (HWAP) of the
                        Division of Hazardous Waste Management, NJDEPE, is pursu-
                        ing the goals of waste  minimization awareness and program
                        implementation in the state. HWAP, with the help of an EPA
                        grant from the Risk Reduction Engineering Laboratory, con-
                        ducted an Assessment of Reduction and Recycling Opportuni-
                        ties for Hazardous Waste (ARROW) project. ARROW was
                        designed to assess waste minimization potential  across a
                        broad range of New Jersey industries. The project targeted 30
                        sites to perform waste minimization assessments following the
                        approach outlined in EPA's Waste Minimization Opportunity
                        Assessment Manual (EPA/625/7-88/003). Under contract to
                        NJDEPE, the Hazardous Substance Management  Research
                        Center at the New Jersey Institute of Technology (NJIT) assisted
                        in conducting the assessments. This research brief presents
                        an assessment of the manufacturing of orthopedic implants for
                        use by  the health care industry (1  of the 30  assessments
                        performed) and provides recommendations for waste minimi-
                        zation options resulting from the assessment.


                        Methodology of Assessments
                        The assessment process was coordinated by a team of techni-
                        cal staff from  NJIT with experience in  process operations,
                        basic chemistry, and environmental concerns and needs. Be-
                        cause the EPA waste minimization manual is designed to be
                        primarily applied by the  inhouse staff of the facility, the degree
                        of involvement of the NJIT team varied according to the ease
                                                                              Printed on Recycled Paper

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 with which the facility staff could apply the manual. In some
 cases,  NJIPs  role was to provide advice.  In  others,  NJIT
 conducted essentially the entire evaluation.

 The goal  of the project  was to encourage participation in the
 assessment process by management and staff at the facility.
 To do this, the participants were encouraged to proceed through
 the organizational steps outlined in the manual. These steps
 can be summarized as follows:

    • Obtaining corporate commitment to a waste minimization
     initiative
    • Organizing a task force or similar group to carry out the
     assessment
    • Developing a policy statement regarding waste  minimiza-
     tion for issuance by corporate management
    • Establishing tentative waste reduction goals to be achieved
     by the program
    • Identifying waste-generating sites and processes
    • Conducting a detailed site inspection
    • Developing a list of options which  may lead to the waste
     reduction goal
    • Formally  analyzing the feasibility of the various options
    • Measuring the effectiveness of the options and continuing
     the assessment.

 Not every  facility was able to follow these steps as presented.
 In  each case, however,  the identification of waste-generating
 sites and processes, detailed site inspections, and development
 of  options  was carried out. Frequently,  it was necessary for a
 high degree of involvement by NJIT to accomplish these steps.
 Two common reasons for needing outside participation were a
 shortage of technical staff within the company and a need to
 develop an agenda for technical action before corporate com-
 mitment and policy statements could be obtained.

 It was not a goal of the ARROW project to participate in the
 feasibility  analysis or  implementation  steps.  However, NJIT
 offered to provide advice for feasibility analysis if requested.

 In  each  case, the NJIT team made several  site visits to the
 facility.  Initially, visits were made to explain the EPA manual
 and to encourage the facility through the organizational stages.
 If delays and complications developed, the team offered assis-
 tance in the technical review, inspections, and option  develop-
 ment.

 No sampling or laboratory analysis was undertaken as part of
 these assessments.


 Facility Background
 The facility is a manufacturer of orthopedic  implants for the
 health care industry. Specific products  include hip, shoulder,
 and knee  replacements made  from  stainless  steel or cobalt
 chromium  alloys. The products are made through a molding
 operation with machining of precision bearings.

 The facility, located in a  suburban  area, employs about 50
 people and has been in its present  location approximately 20
 years.


 Manufacturing Processes
The production of the orthopedic implants is in essence a 3-
step process.  Initially, a wax prototype  with the desired size
 and shape of the finished implant is prepared and all imperfec-
 tions  are repaired  with an alcohol treatment. The wax is then
 coated and gradually a shell is built up with a slurry of colloidal
 silica. The finished shell  is dried in an oven to  produce a
 ceramic mold.

 The ceramic is then  seal-coated  with more silica and then
 placed in an oven to  melt  and drain  the  inner wax and to
 complete  hardening of the  outer shell. A hole is  cut  in the
 ceramic shell to allow draining of the wax and covered  with a
 plastic plug to prevent dirt and other contamination from entering.

 An ingot of either cobalt chromium or stainless steel is melted
 in an electric inductive furnace. The plastic cap is removed
 from the ceramic mold and the molten metal is poured into the
 ceramic cavity.  When  the metal  hardens, the ceramic shell is
 chipped away and  the solid metal implant remains.

 The bearings for the implants  are cut to  precise and specific
 tolerances  using a  computer numerical  control production ma-
 chine. Excess water soluble lubricants used in this process are
 removed  in a 1,1,1-trichloroethane vapor degreasing tank, the
 implant is stencilled for identification, and packaged in plastic
 in a clean room for shipment to the customer.


 Existing  Waste Management Activities
 The company has already  begun consideration of pollution
 prevention options to be used in its processes. One example of
 this consideration is an examination of  the possibility of using
 terpene-based degreasers in place of the chlorinated solvent
 currently used.

 Denatured alcohol is currently used for working the wax molds.
 Annually  about  165 gal of  this  solvent  are  sent  offsite for
 recycling or for recovery of fuel value.

 From the numerically controlled metal machining process 1,155
 gal of water soluble oils and 770 gal of petroleum-based oils
 are generated annually. They are sent  offsite for recycling  or
 fuel value recovery.

 From the  vapor degreaser, 770 gal of 1,1,1-trichloroethane is
 sent offsite for disposal each year. Approximately 400 gal is
 lost annually as  fugitive emissions.


 Waste Minimization Opportunities
 The type  of waste currently generated  by  the facility, the
 source of  the waste, the quantity  of the  waste and the annual
 treatment and disposal costs are given in  Table 1. This particular
 facility is kept scrupulously clean and illustrates that production
 of critical medical products can generate hazardous waste and
 benefit from pollution prevention initiatives.

 Table 2 shows the opportunities for waste minimization recom-
 mended for the  facility. The  type of waste, the minimization
 opportunity, the  possible waste  reduction and associated sav-
 ings, and the implementation cost along  with the payback time
 are given in the table. The quantities of waste currently gener-
 ated at the facility and possible waste reduction depend on the
 level of activity of the facility.

 It should be noted that  the economic savings of the  minimiza-
tion opportunity,  in most cases, results from the need for less
raw material and from reduced present and future costs asso-
ciated  with waste treatment and  disposal. It should also be
noted that the savings given for  each opportunity reflect the

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savings achievable when implementing each waste minimiza-
tion opportunity independently and do not reflect duplication of
savings that would result  when  the opportunities  are imple-
mented in  a  package.  Also,  no equipment depreciation  is
factored into the calculations.


Regulatory Implications
There are no significant regulatory issues which would impede
the introduction of further pollution prevention concepts at this
facility. Increased regulatory concern about releases of chlori-
nated hydrocarbons may accelerate the investigation of pos-
sible use of terpenic or alkaline aqueous degreasing systems.
Use of terpenic material  for this purpose may eventually raise

* Mention of trade names or commercial products does not constitute endorsement
 or recommendation for use.
                                        questions about the advisability of discharging such materials
                                        to a POTW,  even though they are usually naturally occurring
                                        materials.

                                        This Research Brief summarizes a part of the work done under
                                        cooperative Agreement No.  CR-815165 by the New Jersey
                                        Institute  of  Technology  under the  sponsorship of the New
                                        Jersey Department of Environmental  Protection and Energy
                                        and the U.S. Environmental Protection Agency. The EPA Project
                                        Officer was Mary Ann Curran. She can be reached  at:

                                                 Pollution Prevention Research Branch
                                                 Risk Reduction Engineering Laboratory
                                                 U.S. Environmental Protection Agency
                                                 Cincinnati, OH 45268
Table 1. Summary of Current Waste Generation
Waste Generated
                       Source of Waste
                                 Annual Quantity
                                    Generated
                    Annual Waste
                  Management Costs
Chlorinated Solvent
                      Effluent from vapor degreaser
                                     770 gal
                        $2,450
Chlorinated Solvent


Denatured Alcohol

Water Soluble Oils

Petroleum Oils
Evaporative losses from
solvent degreaser

Wax mold working

Metal machining

Lubrication
 400 gal


 165 gal

1155 gal

 770 gal
    2,600
(raw material loss)

     525

    3,675

    2,450
                                                                                 •U.S. Government Printing Office: 1992 — 648-080/60125

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Table 2.  Summary of Recommended Waste Minimization Opportunities
Waste Stream
Reduced
 Chlorinated Solvent
Denatured Alcohol
Water Soluble Oils
Minimization Opportunity
Acquisition of onsite distilla-
tion equipment to recycle
and reuse degreasing solvents.

Continue investigation of change
to alkaline aqueous based or
terpene based degreasers.  Ultra-
sonic bath in combination with
the alkaline aqueous based degreaser
may be most effective.

Recycle and reuse this solvent by
onsite distillation.

Segregate and use onsite recovery
and recycling service.
 Annual Waste Reduction
Quantity       Percent
                                                         616 gal
                                                        1170 gal
  132 gal


  925 gal
                80
               100
                                                                        80
                                                                        80
     Net        Implementation   Payback
Annual Savings        Cost      Years'
   $5,960
                                9,957
                                                                                         820
                                                                                       2,940
                                             $4,000
                   3,500
0.6
0.3
                                                                                                      4,000
                                 5.0
                                 immed
* Savings result from reduced raw material and treatment and disposal costs when implementing each minimization opportunity independently.
  United States
  Environmental Protection Agency
  Center for Environmental Research Information
  Cincinnati, OH 45268

  Official Business
  Penalty for Private Use
  $300
                                                                               BULK RATE
                                                                         POSTAGE & FEES PAID
                                                                                   EPA
                                                                             PERMIT No. G-35
  EPA/600/S-92/064

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