United States
             Agency
             Industry
 SECTOR
NOTEBCXDKS

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                 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
                                WASHINGTON, D.C. 20460
                                                                         THE ADMINISTRATOR
Message from the Administrator

Over the past 25 years, our nation has made tremendous progress in protecting public health and
our environment while promoting economic prosperity. Businesses as large as iron and steel
plants and businesses as small as the dry cleaner on the corner have worked with EPA to find
ways to operate cleaner, cheaper, and smarter. As a result, we no longer have rivers catching on
fire. Our skies are clearer. American environmental technology and expertise are in demand
throughout the world.

The Clinton Administration recognizes that to continue this progress, we must move beyond the
pollutant-by-pollutant approaches of the past to comprehensive, facility-wide approaches for the
future. Industry by industry and community by community, we must build a new generation of
environmental protection.

Within the past two years, the Environmental Protection Agency undertook its Sector Notebook
Project to compile, for a number of key industries, information about environmental problems and
solutions, case studies and tips about complying with regulations. We called on industry leaders,
state regulators, and EPA staff with many years of experience in these industries and with their
unique environmental issues. Together with notebooks for 17 other industries, the notebook you
hold in your hand is the result.

These notebooks will help business managers to better understand their regulatory requirements,
learn more about how others in their industry have undertaken regulatory compliance and the
innovative methods some have found to prevent pollution in the first instance. These notebooks
will give useful information to state regulatory agencies moving toward industry-based programs.
Across EPA we will use this manual to better integrate our programs and improve our compliance
assistance efforts.

I encourage you to use this notebook to evaluate and improve the way that together we achieve
our important environmental protection goals. I am confident that these notebooks will help us to
move forward in ensuring that — in industry after industry, community after community ~
environmental protection and economic prosperity go hand in hand.
                                                Carol M. Brown
           Recycled/Recyclable • Printed with Vegetable Based Inks on Recycled Paper (20% Postconsumer)

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Fabricated Metal Products
                                                     Sector Nolebool Project
                                                     EPA/310-R-95-007
    EPA Office  of Compliance  Sector Notebook
                             Project

                 Profile  of  the Fabricated
                 Metal  Products  Industry
                            September 1995
                         Office of Compliance
             Office of Enforcement and Compliance Assurance
                  U.S. Environmental Protection Agency
                       401 M St., SW (MC 2221-A)
                        Washington, DC 20460
                       For sale by the U.S. Government Printing Office
                Superintendent of Documents, Mail Stop: SSOP, Washington, DC 20402-9328
                           ISBN 0-16-048274-7
SIC Code 34
September 1995

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Sector Notebook Project
          Fabricated Metal Products
This report is one in a series of volumes published by the U.S. Environmental
Protection Agency (EPA) to provide information of general interest regarding
environmental issues associated with specific industrial sectors.  The documents
were developed under contract by Abt Associates (Cambridge, MA), and Booz-
Allen & Hamilton, Inc. (McLean, VA). This publication may be purchased from
the Superintendent of Documents, U.S. Government Printing Office.  A listing of
available Sector Notebooks and document numbers is included at the end of this
document.
All telephone orders should be directed to:

      Superintendent of Documents
      U.S. Government Printing Office
      Washington, DC 20402
      (202) 512-1800
      FAX (202) 512-2250
      8:00 a.m.  to 4:30 p.m., EST, M-F
Using the form provided at the end of this document, all mail orders should be
directed to:

      U.S. Government Printing Office
      P.O. Box 371954
      Pittsburgh, PA 15250-7954


Complimentary volumes are available to certain groups or subscribers, such as
public and academic libraries, Federal, State, local, and foreign governments, and
the media.  For further information, and for answers to questions pertaining to
these documents, please refer to the contact names and numbers provided
within this  volume.
Electronic versions of all Sector Notebooks are available on the EPA Enviro$en$e
Bulletin Board and via  Internet  on the  Enviro$en$e World  Wide  Web.
Downloading procedures are described in Appendix A of this document.
Cover photograph by Steve Delaney, U.S. EPA.
Atlantic  Finishing,  Capitol  Heights, Maryland.
Photograph courtesy of Mi'd-
Septemberl995
                                                                     SIC 34

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                                      Sector Notebook Contacts

 The Sector Notebooks were developed by the EPA's Office of Compliance. Particular questions regarding the
 Sector Notebook Project in general can be directed to:

         Seth Heminway, Sector Notebook Project Coordinator
         US EPA, Office of Compliance
         401 M St., SW (2223-A)
         Washington, DC 20460
         (202) 564-7017 fax (202) 564-0050
         E-mail: heminway.seth@epamail.epa.gov

 Questions and comments regarding the individual documents can be directed to the appropriate specialists listed
 below.
 Document Number
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-

 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310-
 EPA/310
•R-95-001.
R-95-002.
R-95-003.
-R-95-004.
-R-95-005.
-R-95-006.
-R-95-007.
-R-95-008.
-R-95-009.
-R-95-010.
-R-95-011.
-R-95-012.
-R-95-013.
•R-95-014.
-R-95-015.
-R-95-016.
•R-95-017.
-R-95-018.

•R-97-001.
•R-97-002.
•R-97-003.
-R-97-004.
•R-97-005.
-R-97-006.
R-97-007.
•R-97-00.8.
R-97-009.
•R-97-010.
EPA/310-B-96-003.
    Industry

  Dry Cleaning Industry
  Electronics and Computer Industry
  Wood Furniture and Fixtures Industry
  Inorganic Chemical Industry
  Iron and Steel Industry
  Lumber and Wood Products Industry
  Fabricated Metal Products Industry
  Metal Mining Industry
  Motor Vehicle Assembly Industry
  Nonferrous Metals Industry
  Non-Fuel, Non-Metal Mining Industry
  Organic Chemical Industry
  Petroleum Refining Industry
  Printing Industry
  Pulp and Paper Industry
  Rubber and Plastic Industry
  Stone, Clay, Glass, and Concrete Industry
  Transportation Equipment Cleaning Ind.

*Air Transportation Industry
  Ground Transportation Industry
*Water Transportation Industry
  Metal Casting Industry
  Pharmaceutical Industry
  Plastic Resin and Man-made Fiber Ind.
*Fossil Fuel  Electric Power Generation Ind.
*Shipbuilding and Repair Industry
  Textile Industry
* Sector Notebook Data Refresh, 1997

  Federal Facilities
 Contact

 Joyce Chandler
 Steve Hoover
 Bob Marshall
 Walter DeRieux
 Maria Malave
 Seth Heminway
 Scott Throwe
 Keith Brown
 Suzanne Childress
 Jane Engert
 Keith Brown
 Walter DeRieux
 Tom Ripp
 Ginger Gotliffe
 Maria Eisemann
 Maria Malave
 Scott Throwe
 Virginia Lathrop

 Virginia Lathrop
 Virginia Lathrop
 Virginia Lathrop
 Jane Engert
 Emily Chow
 Sally Sasnett
 Rafael Sanchez
 Suzanne Childress
 Belinda Breidenbach
 Seth Heminway

Jim Edwards
 Phone (202)

 564-7073
 564-7007
 564-7021
 564-7067
 564-7027
 564-7017
 564-7013
 564-7124
 564-7018
 564-5021
 564-7124
 564-7067
 564-7003
 564-7072
 564-7016
 564-7027
 564-7013
 564-7057

 564-7057
 564-7057
 564-7057
 564-5021
 564-7071
 564-7074
 564-7028
 564-7018
 564-7022
564-7017

 564-2461
*Currently in DRAFT anticipated publication in September 1997
This page updated during June 1997 reprinting

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Fabricated Metal Products
                  Sector Notebool Project
                       FABRICATED METAL PRODUCTS
                                 (SIC 34)
                           TABLE OF CONTENTS
                                                                    Page
EXHIBIT INDEX	vn
LIST OF ACRONYMS	ix
I.     INTRODUCTION OF THE SECTOR NOTEBOOK PROJECT	I
      LA.    Summary of the Sector Notebook Project	I
      LB.    Additional Information	2
n.    INTRODUCTION TO THE FABRICATED METAL PRODUCTS INDUSTRY	4
      n.A.   Introduction, Background, and Scope of the Notebook	4
      n.B.    Characterization of the Fabricated Metal Products Industry	4
             n.B.l.    Industry Size and Geographic Distribution	4
             n.B.2.    Product Characterization	9
             H.B.3.    Economic Trends	9
m.   INDUSTRIAL PROCESS DESCRIPTION	12
      EI.A.  Industrial Processes in the Fabricated Metal Products
             Industry	12
             ffi.A.l.   Fabricated Metal Products	13
             IE.A.2.   Surface Preparation	15
             IE.A.3.   Metal Finishing	16
      ITLB.  Raw Material Inputs and Pollution Outputs in the
             Production Line	•	21
             m.B.l.   Metal Fabrication	24
             in.B.2.   Surface Preparation	25
             m.B.3.   Metal Finishing	25
             Management of Chemicals in Wastestream	29
SIC Code 34
IV
September 1995

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Sector Notebook Project
                                                Fabricated Metal Products
IV.
V.
VI.
                       FABRICATED METAL PRODUCTS
                                  (SIC 34)
                       TABLE OF CONTENTS (CONT'D)
                                                                    Page
CHEMICAL RELEASE AND TRANSFER PROFILE	31
IV.A.   EPA Toxic Release Inventory for the Fabricated Metal
        Products Industry	34
IV.B.   Summary of the Selected Chemicals Released	46
FV.C.   Other Data Sources	53
IV.D.   Comparison of Toxic Release Inventory Between Selected
        Industries	55
POLLUTION PREVENTION OPPORTUNITIES	58
V.A.    Identification of Pollution Prevention Activities in Use and
        Environmental and Economic Benefits of Each Pollution
        Prevention Activity	58
V.B.    Possible Pollution Prevention Future Trends	61
V.C.    Pollution  Prevention Case Studies	62
V.D.    Pollution  Prevention Options	65
        V.D.I.   Metal Shaping Operations	65
        V.D.2.   Surface Preparation Operations	67
        V.D.3.   Plating Operations	71
        V.D.4.   Other Finishing Operations	75
V.E.    Pollution  Prevention Contacts	78
SUMMARY OF APPLICABLE FEDERAL STATUTES AND REGULATIONS	80
VI.A.   General Description of Major Statutes	80
VLB.    Industry Specific Regulations	92
VI.C.    Pending and Proposed Regulatory Requirements	97
September 1995
                                                          SIC Code 34

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Fabricated Metal Products
Sector Notebool Project
                      FABRICATED METAL PRODUCTS
                                (SIC 34)
                      TABLE OF CONTENTS (CONT'D)
                                                                  Page
VII.   COMPLIANCE AND ENFORCEMENT PROFILE	100

      VILA.  Fabricated Metal Products Industry Compliance History	104

      VII.B.  Comparison of Enforcement Activity Between
             Selected Industries	104

      VTI.C.  Review of Major Legal Actions	Ill
             VII.C.l   Review of Major Cases	Ill
             VH.C.2   Supplemental Environmental Projects	112

VIH.  COMPLIANCE ACTIVITIES AND INITIATIVES	116

      VIILA. Sector-Related Environmental Programs and Activities	116

      Vin.B. EPA Voluntary Programs	122

      Vm.C. Trade Association/Industry Sponsored Activity	132
             Vm.C.l.  Environmental Programs	132
             VHLC.2.  Summary of Trade Associations	134

IX.    CONTACTS/ACKNOWLEDGMENTS/RESOURCE MATERIALS/
      BIBLIOGRAPHY AND OTHER REFERENCES	138
SIC Code 34
                                     VI
      September 1995

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Sector Notebook Project
                   Fabricated Metal Products
                         FABRICATED METAL PRODUCTS
                                    (SIC 34)
                                EXHIBIT INDEX
                                                                         Page
Exhibit 1    Metal Fabrication Companies	5
Exhibit 2    Number of Employees in Metal Finishing Industry	5
Exhibits    Value of Shipments for Metal Finishing Establishments	6
Exhibit 4    Inorganic Coating Job Shops	6
Exhibit 5    Organic Coating Job Shops	6
Exhibit 6    Metal Finishing Establishments, by Size	7
Exhibit 7    Geographic Distribution of Fabricated Metal Products Industry	7
Exhibit 8    Markets Served by Metal Finishers	10
Exhibit 9    Forming Operations	14
Exhibit 10   Rolling	14
Exhibit 11   Process for Preparing Metal for Electroplating	15
Exhibit 12   Overview of the Metal Finishing Process	16
Exhibit 13   Typical Electroplating Equipment	18
Exhibit 14   Electroless Plating Process	19
Exhibit 15   Process Materials Inputs and Outputs	22
Exhibit 16   Fabricated Metal Products Manufacturing Processes	23
Exhibit 17   Typical Metal Finishing Process Step	26
Exhibit 18   Source Reduction and Recycling Activity for SIC 34	30
Exhibit 19   Top 10 TRI Releasing Fabricated Metal Products Facilities	35
Exhibit 20   Top 10 TRI Releasing  Metal  Fabricating & Finishing
             Facilities (SIC 34)	36
Exhibit 21   Reductions in TRI Releases, 1988-1993 (SIC 34)	36
Exhibit 22   Reductions in TRI Transfers, 1988-1993 (SIC 34)	36
Exhibit 23   TRI Reporting Metal Fabricating & Finishing Facilities
             (SIC 34) by State	37
Exhibit 24   Releases for  Metal Fabricating & Finishing Facilities (SIC 34)
             in TRI, by Number of Facilities (Releases
             reported in pounds/year)	38,39
Exhibit 25   Transfers for Metal Fabricating  & Finishing Facilities (SIC  34) in
             TRI, by Number of Facilities (Transfers reported
             in pounds/year)	40,41
Exhibit 26   Top 10 TRI Releasing Metal Finishing Facilities (SIC 347)	42
Exhibit 27   TRI Reporting Metal Finishing Facilities (SIC 347) by State	43
Exhibit 28   Releases for  Metal Finishing (SIC 347) in TRI, by Number  of
             Facilities (Releases reported in pounds/year)	43,44
September 1995
vn
                             SIC Code 34

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Fabricated Metal Products
                   Sector Notebool Project
                       FABRICATED METAL PRODUCTS
                                  (SIC 34)
                          EXHIBIT INDEX (CONT'D)
                                                                      Page
Exhibit 29   Transfers for Metal Finishing (SIC 347) in TRI, by Number of
            Facilities (Transfers reported in pounds/year)	45,46
Exhibit 30   Pollutant Releases (Short Tons/Year)	54
Exhibit 31   Summary of 1993 TRI Data	56
Exhibit 32   Toxic Releases Inventory for Selected Industries	57
Exhibit 33   Hazardous Wastes Relevant to the Metal
            Finishing Industry	96,97
Exhibit 34   Five Year Enforcement and Compliance Summary
            for Fabricated Metal Products Industry 	106
Exhibit 35   Five Year Enforcement and Compliance Summary for
            Selected Industries	107
Exhibit 36   One Year Enforcement and Compliance Summary for
            Selected Industries	108
Exhibit 37   Five Year Inspection and Enforcement Summary by Statute
            for Selected Industries	109
Exhibit 38   One Year Inspection and Enforcement Summary by Statute
            for Selected Industries	110
Exhibit 39   Supplemental Environmental  Projects	113,114,115
Exhibit 40   Fabricated Metal Producers Participating in the
            33/50 Program	123-129
 SIC Code 34
Vlll
September 1995

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Sector Notebook Project
                 Fabricated Metal Products
                       FABRICATED METAL PRODUCTS
                                 (SIC 34)
                            LIST OF ACRONYMS

APS -       AIRS Facility Subsystem (CAA database)
AIRS -      Aerometric Information Retrieval System (CAA database)
BIFs -       Boilers and Industrial Furnaces (RCRA)
BOD -       Biochemical Oxygen Demand
CAA -       Clean Air Act
CAAA -     Clean Air Act Amendments of 1990
CERCLA-   Comprehensive Environmental Response, Compensation and
            Liability Act
CERCLIS -   CERCLA Information System
CFCs -       Chlorofluorocarbons
CO -        Carbon Monoxide
COD -       Chemical Oxygen Demand
CSI-       Common Sense Initiative
CWA -      Clean Water Act
D&B -       Dun and Bradstreet Marketing Index
ELP-       Environmental Leadership Program
EPA -       United States Environmental Protection Agency
EPCRA -    Emergency Planning  and Community Right-to-Know Act
FIFRA -     Federal Insecticide, Fungicide, and Rodenticide Act
FINDS -     Facility Indexing System
HAPs -      Hazardous Air Pollutants (CAA)
HSDB -     Hazardous Substances Data Bank
IDEA -      Integrated Data for Enforcement Analysis
LDR -       Land Disposal Restrictions  (RCRA)
LEPCs -     Local Emergency Planning Committees
MACT -     Maximum Achievable Control Technology (CAA)
MCLGs -    Maximum Contaminant Level Goals
MCLs-      Maximum Contaminant Levels
MEK -       Methyl Ethyl Ketone
MSDSs -    Material Safety Data Sheets
NAAQS -   National Ambient Air Quality Standards (CAA)
NAFTA -   North American  Free Trade Agreement
NCDB -     National Compliance Database (for TSCA, FIFRA, EPCRA)
NCP -       National Oil and Hazardous Substances Pollution Contingency
            Plan
NEIC -      National Enforcement Investigation Center
NESHAP -   National Emission Standards for Hazardous Air Pollutants
NO2-       Nitrogen Dioxide
NOV -      Notice of Violation
NOX -       Nitrogen Oxide
NPDES -    National Pollution Discharge Elimination System (CWA)
September 1995
IX
                           SIC Code 34

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Fabricated Metal Products
Sector Notebool Project
                       FABRICATED METAL PRODUCTS
                                 (SIC 34)
                        LIST OF ACRONYMS (CONT'D)

NPL -       National Priorities List
NRC -      National Response Center
NSPS -      New Source Performance Standards (CAA)
OAR -      Office of Air and Radiation
OECA -     Office of Enforcement and Compliance Assurance
OPA -      Oil Pollution Act
OPPTS -     Office of Prevention, Pesticides, and Toxic Substances
OSHA -     Occupational Safety and Health Administration
OSW -      Office of Solid Waste
OSWER -    Office of Solid Waste and Emergency Response
OW -       Office of Water
P2-        Pollution Prevention
PCS -       Permit Compliance System (CWA Database)
POTW -     Publicly Owned Treatments Works
RCRA -     Resource Conservation and Recovery Act
RCRIS -     RCRA Information System
SARA -     Superfund Amendments and Reauthorization Act
SDWA -     Safe Drinking  Water Act
SEPs-      Supplementary Environmental Projects
SERCs -     State Emergency Response Commissions
SIC -        Standard Industrial Classification
SOi-        Sulfur Dioxide
TOC -      Total Organic Carbon
TRI -        Toxic Release  Inventory
TRIS -      Toxic Release  Inventory System
TCRIS -     Toxic Chemical Release Inventory System
TSCA -     Toxic Substances Control Act
TSS -       Total Suspended Solids
UIC -       Underground  Injection Control (SDWA)
UST -      Underground  Storage Tanks (RCRA)
VOCs -     Volatile Organic Compounds
 SIC Code 34
      September 1995

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fabricated Metal Products
                                                        Sector Notebook Project
                    FABRICATED METAL PRODUCTS
                                 (SIC 34)


I.     INTRODUCTION OF THE SECTOR NOTEBOOK PROJECT

I.A.   Summary of the Sector Notebook Project

            Environmental policies based upon comprehensive analysis of air,
            water, and  land pollution are an inevitable and logical supplement
            to  traditional  single-media  approaches  to  environmental
            protection.   Environmental regulatory agencies  are  beginning to
            embrace comprehensive, multi-statute  solutions to  facility
            permitting,  enforcement   and   compliance   assurance,
            education/outreach, research, and  regulatory development issues.
            The central concepts driving the  new  policy direction are that
            pollutant releases to each  environmental medium (air, water, and
            land)  affect each other, and that  environmental strategies must
            actively identify and address these  inter-relationships by designing
            policies for  the "whole" facility. One way to achieve a  whole facility
            focus  is to  design  environmental policies for  similar  industrial
            facilities. By doing so, environmental concerns that are common to
            the manufacturing  of similar products can be  addressed in  a
            comprehensive manner.  Recognition of the need to develop  the
            industrial  "sector-based"  approach within  the EPA  Office  of
            Compliance led to the creation of this document.

            The Sector  Notebook Project was  initiated by the  Office  of
            Compliance within the Office of  Enforcement  and  Compliance
            Assurance (OECA) to provide its staff and managers with summary
            information for eighteen specific industrial sectors. As other EPA
            offices, States, the regulated community, environmental  groups,
            and the public became interested in this project, the scope of  the
            original  project  was expanded.    The  ability  to  design
            comprehensive,  common   sense  environmental  protection
            measures for specific industries is dependent  on knowledge  of
            several inter-related topics. For the  purposes of this project, the key
            elements chosen for inclusion are:  general industry information
            (economic and geographic); a description of industrial processes;
            pollution outputs;  pollution prevention opportunities;  Federal
            statutory and  regulatory framework; compliance history; and  a
            description  of  partnerships that have been  formed between
            regulatory agencies, the regulated community, and the  public.

            For any given industry, each topic  listed above could alone be  the
            subject of a lengthy volume.   However, in  order to produce  a
September 1995
SIC Code 34

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Fabricated Metal Products
Sector Notebook Project
            manageable document, this project focuses on providing summary
            information for each topic.  This format provides the reader with a
            synopsis  of each  issue,  and references where  more  in-depth
            information is available.  Text within each profile  was researched
            from a variety of sources, and was usually condensed from more
            detailed sources pertaining to specific topics.  This approach allows
            for a wide coverage of activities that can be further explored based
            upon the citations and references listed at the end of this profile.  As
            a check on the information included, each notebook went through
            an external review  process.  The Office of Compliance appreciates
            the efforts of all those that participated in this process and enabled
            us to develop more complete, accurate, and up-to-date summaries.
            Many of those who reviewed this notebook are listed as contacts in
            Section IX and may be sources of additional information.   The
            individuals and groups on this list do not necessarily concur with
            all statements within this notebook.
I.E.   Additional Information

Providing Comments

            OECA's  Office of Compliance  plans to periodically review  and
            update the notebooks and will make these updates available both in
            hard copy and electronically.  If you have any comments on the
            existing  notebook, or  if you would like  to  provide additional
            information, please send a hard copy and computer disk to the EPA
            Office  of Compliance, Sector Notebook Project, 401 M St., SW (2223-
            A), Washington, DC 20460.  Comments can also be uploaded to the
            Enviro$en$e  Bulletin Board or the Enviro$en$e World Wide Web
            for general access to all users  of the system.  Follow instructions in
            Appendix A for accessing these data systems.  Once you have logged
            in, procedures for uploading text are available  from  the on-line
            Enviro$en$e  Help System.

Adapting Notebooks to Particular Needs

            The scope of the existing notebooks  reflect an approximation of the
            relative national occurrence of facility types that occur within each
            sector. In many  instances, industries within specific geographic
            regions or States may have unique characteristics that are not fully
            captured in these profiles. For this reason, the Office of Compliance
            encourages  State and local  environmental agencies and other
            groups to  supplement or re-package the information included in
            this notebook to include more specific industrial and regulatory
            information that may be available.  Additionally, interested States
SIC Code 34
       September 1995

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TJafeiicatecL Metal Products
                                                           Sector Notebook Project
             may want to supplement  the  "Summary of Applicable  Federal
             Statutes  and  Regulations"   section  with  State  and  local
             requirements.  Compliance or technical assistance providers may
             also  want to develop the "Pollution Prevention"  section in more
             detail.  Please contact the appropriate specialist listed on the opening
             page of this notebook if your office is interested in assisting us in the
             further development  of the information or policies addressed
             within this volume.

             If you are  interested in assisting in the  development of new
             notebooks for sectors not covered  in the original  eighteen, please
             contact the Office of Compliance at 202-564-2395.
September 1995
SIC Code 34

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Fabricated Metal Products
Sector Notebook Project
      INTRODUCTION TO THE FABRICATED METAL PRODUCTS INDUSTRY

            This  section  provides  background  information  on  the size,
            geographic distribution,  employment,  production, sales,  and
            economic condition of the Fabricated Metal Products industry.  The
            types of facilities described within the document are also described
            in terms of their Standard Industrial Classification (SIC) codes.
            Additionally, this section contains a list of the largest companies in
            terms of sales.
II.A.  Introduction, Background, and Scope of the Notebook

            The fabricated metal products industry comprises facilities that
            generally perform two functions:   forming metal  shapes and
            performing metal  finishing operations,  including  surface
            preparation. The Standard Industrial Classification (SIC) code 34 is
            composed of establishments that fabricate ferrous and nonferrous
            metal products and those that perform electroplating,  plating,
            polishing, anodizing, coloring, and coating operations on metals.
            Since the main processes  associated with this  industry can  be
            divided into three types of operations (i.e., metal fabrication, metal
            preparation, and metal finishing), this profile is organized by the
            techniques that fall within these three groups.


II.B.  Characterization of the Fabricated Metal Products Industry

            To provide a general understanding of this industry, information
            pertaining  to  the  industry  size and distribution,  product
            characterization, and economic health  and outlook is presented
            below.  This information should provide a basic understanding of
            the facilities developing the products, the products themselves, and
            the economic condition of the industry.

H.B.I. Industry Size and Geographic  Distribution

            Variation in facility counts occur across data  sources due  to many
            factors,  including reporting  and  definitional  differences.  This
            document does not attempt to  reconcile these differences, but rather
            reports the  data as they are maintained by each source.

            The  U.S.  fabricated metal  products  industry   comprises
             approximately 34,000  companies. Exhibit 1  lists the largest
             companies  in selected metal fabricating industries.  Companies  are
             ranked by sales figures.
 SIC Code 34
                                                                September 1995

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Fabricated Metal Products
                                                            Sector Notebook Project
                                   Exhibit!
                         Metal Fabrication Companies
                    Company
   Sales
($ Millions)
Number of
Employees
SIC 3444 - Sheet Metal Work
Stolle Corp., Sidney, OH
Alcan Alum. Corp., Warren, OH
Nytronics, Inc., Pitman, NJ
Hart and Cooley Inc., Holland, MI
Syro Steel Co., Girard, OH
Consolidated Systems, Inc., Columbia, SC
480
120
110
100
100
100
4,600
1,200
2,000
1,200
400
300
SIC 3465 — Automotive Stampings
Budd Co., Troy, MI
Douglas and Lomason Co., Farmington Hts., MI
Northern Engraving Corp., Sparta, WI
Randall Textron Inc., Cincinnati, OH
1,000
391
280
210
9,000
5,800
3,000
2,000
SIC 3469 — Metal Stampings
Hexcel Corp., Pleasanton, CA
JSJ Corp., Grand Haven, MI
Mirro-Foley Co., Manitowoc, WI
Tempel Steel Co., Niles, IL
386
260
210
210
2,900
2,500
2,000
1,100
SIC 3499 - Fabricated Metal Products
Steel Technologies, Louisville, KY
R.D. Werner Company, Inc., Greenville, PA
BW/IP Int., Inc., Seal Div., Long Beach, CA
LeFebure Corp., Cedar Rapids, IA
Dura Mech. Components, Inc., Troy, MI
155
150
104
100
100
500
1,600
400
1,100
1,000
                     Source:  Fabricators & Manufacturers Association, Intl.

             Exhibits 2 and 3 show the distribution of employees and the total
             shipments for the metal finishing industry.  A  typical "job shop"
             (i.e., small,  independently owned  metal  finishing company)
             employs 15 to 20 people  and generates $800,000 to $1 million in
             annual gross revenues.
                                  Exhibit 2
               Number of Employees in Metal Finishing Industry

SIC 3471
SIC 3479
Total
1988
76,300
47,000
123,300
Source: U.S.
1989
76,600
44,600
121,200
1990
73,200
44,300
117,500
1991
66,600
43,400
110,000
1992
65,400
43,700
109,100
Department of Commerce, 1992 Census of Manufacturers.
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Fabricated Metal Products
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                                    Exhibit 3
      Value of Shipments for Metal Finishing Establishments ($ Millions)

SIC 3471
SIC 3479
Total
1988
4,324
4,867
9,191
1989
4,452
4,756
9,208
1990
4,513
4,929
9,442
1991
4,124
4,634
8,758
1992
4,726
5,161
9,887
                Source: U.S. Department of Commerce, 1992 Census of Manufacturers.

             Exhibits 4  and 5 list  the largest companies in  selected  metal
             finishing industries.  Companies are ranked by sales figures.
                                    Exhibit 4
                          Inorganic Coating Job Shops
Company
Windsor Plastics, Evansville, EM
Crown City Plating, El Monte, CA
Pioneer Metal Finishing, Minneapolis, MN
Metal Surfaces, Bell Gardens, CA
Victory Finishing Technologies, Inc., Providence,
RI
State Plating, Inc., Elwood, IN
Sales
($ Millions)
50
25
20-30
15-25
15-25
15-20
Number of
Employees
600
425
380
310
245
400
          Source:  Large Plating Job Shops,  Beverly A. Greaves, Products timsmng, April
                                    Exhibit 5
                           Organic Coating Job Shops
Company
Metokote Corp., Lima, OH
The Crown Group, Warren, MI
Industrial Powder Coatings, Inc., Norwalk, OH
PreFinish Metals, Chicago, IL
E/M Corp., West Lafayette, IN
Chicago Finished Metals, Bridgeview, IL
Linetec Co., Wausau, WI
B.L. Downey Co., Inc., Broadview, IL
Sales
($ Millions)
25+
25+
25+
25+
15-25
25+
10-15
10-15
Number of
Employees
800
659
620
600
300
250
200
175
        Source:  "Large Coating fob Shops, Beverly A. Greaves, froaucts finishing, uecemoer

             Between 1982 and 1987, the total number  of independent metal
             finishers employing less than 20 employees declined slightly, while
             those  employing  more  than 20 employees  increased by  a
             corresponding amount.  Exhibit 6 shows the number and percent of
             metal finishers of various sizes.
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 Patyticated. Metal Piochicts
                                                              Sector Notebook Project
                                     Exhibit 6
              Metal Finishing Establishments,, by Size
1987
Establishments With
and Average of :
1 to 9 Employees
10 to 49 Employees
50 to 99 Employees
100 to 249 Employees
250 or more Employees
Total
Number of
Companies
2481
2262
365+
137
20
5265
Percent Total
47.1
43.0
6.9
2.6
0.4
100.0
1992
Number of
Companies
2553
2186
381
356
127
5603
Percent
Total
48.7
41.7
6.8
2.4
0.4
100.0
             source: census of Manufacturers: LWl, U. b. Department of Commerce, Bureau of the Census

             Although the metal finishing industry is geographically diverse, the
             industry is concentrated in what are usually considered the most
             heavily  industrialized regions in the United States  (See Exhibit 7).
             This  geographic concentration  occurs in part  because  it is cost-
             effective for small metal  finishing facilities to be located near their
             customer base.
                                    Exhibit 7
          Geographic Distribution of Fabricated Metal Products Industry
                          Source: Census of Manufacturers: 1987.
             California has more  establishments  that produce  metal-related
             products  than  any  other State.   California's  establishments
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            constitute 10.2 percent of the total establishments that produce
            fabricated structural metal (SIC 3441).  In addition, California leads
            in the number of establishments of other related industries:  15.6
            percent of the  sheet  metal work establishments (SIC 3444);  13
            percent of the metal doors, sash, and trim establishments (SIC 3442);
            and 13.7 percent of the architectural metal work establishments
            (SIC 3446).  California also has the majority of plating and polishing
            (SIC 3471)  and  metal coating  and  allied  services  (SIC 3479)
            establishments at 17.3 and 16.1 percent, respectively.

            Michigan, Illinois, and Ohio have large numbers of various metal-
            related industries.  Michigan has the largest number of companies
            in  the screw  machine  products (SIC 3451)  and  automotive
            stampings (SIC 3465) industries, at  14 and 46.7 percent of the  total
            companies in the United States, respectively.  Illinois is home to
            14.1 percent of companies that produce bolts, nuts, rivets, and
            washers (SIC 3452) and Ohio contains 12.6 percent of companies that
            produce iron and steel forgings (SIC 3462).

            Establishments  engaged primarily in metal finishing tend to  be
            small, independently  owned job shops,  also  are referred to as
            independent metal finishers.  Establishments  that conduct metal
            finishing operations as part of a larger manufacturing operation are
            referred  to as "captive" metal finishers.  Captive metal  finishing
            facilities are approximately three times  more numerous  than
            independent metal finishers.  Numerous similarities exist between
            the  independent and  captive facilities; for the purposes  of this
            profile, they  are considered part of one industry. In addition, the
            two segments have parallel ties with suppliers and  customers.
            Captive  operations may be  more  specialized in their operations,
            however, because they often work on a limited number of products
            and/or employ a limited number of processes.  Independent metal
            finishers, on  the other hand, tend to be less  specialized in  their
            operations because they may have  many  customers,  often  with
            different requirements.
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II.B.2. Product Characterization
            The Department of Commerce classification codes  divide this
            industry by product and services.  SIC code 34 is further divided as
            follows:

                  SIC 341  -  Metal Cans and Shipping Containers
                  SIC 3.42  -  Cutlery, Handtools, and General Hardware
                  SIC 343  -  Heating Equipment, Except Electric and Warm
                              Air, and Plumbing Fixtures
                  SIC 344  -  Fabricated Structural Metal Products
                  SIC 345  -  Screw Machine Products, and Bolts, Nuts,
                              Screws, Rivets, and Washers
                  SIC 346  -  Metal Forgings and Stampings
                  SIC 347  -  Coating, Engraving, and Allied Services
                  SIC 348  -  Ordnance and Accessories, Except Vehicles and
                              Guided Missiles
                  SIC 349  -  Miscellaneous Fabricated Metal Products.
II.B.3. Economic Trends
            Most industries in SIC 34 are largely dependent upon the demands
            of other industries.  For example, the success of the  commercial
            construction industry is fundamental to the success of the fabricated
            structural metal industry; 95 percent of the output from the latter is
            consumed by  the former.   The  general component-producing
            industries (e.g., screw machine products, industrial fasteners, etc.)
            display the same demand structure; the demand for such products is
            directly related to the demand for automobiles and public works
            construction.

            Fabricated structural metal output declined two percent in 1993 due
            to a decrease  in construction  of office buildings,  commercial
            structures, manufacturing facilities,  and multi-family  housing.
            Ninety-five percent of structural  metal output is consumed by the
            construction industry.  Low demand for structural metal is expected
            to continue, attributable to the recent overbuilding of  commercial
            space and high levels of vacant office space.  A slight increase in
            demand from  the public sector (e.g., highway  construction)  is
            expected, however, which will  positively influence demand for
            structural metal products.  An  increased demand for plumbing
            products  is also  likely, as the residential construction industry
            continues to grow.
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Fabricated Metal Products
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             Total shipments of  general components  (e.g., screw machine
             products, industrial fasteners, valves, and pipe fittings) increased by
             about 3.1 percent  in  1993.  Strong demand from  the automotive
             sector,  combined  with increased  demand from equipment and
             machinery  manufacturers, were the  major  factors  causing  the
             increased shipments.

             The  two primary markets for  metal finishing services are  the
             automotive and  electronics industries.  As illustrated in Exhibit 8,
             consumer durables, aerospace, and the government also are large
             segments served by metal finishers.
                                   Exhibits
                       Markets Served by Metal Finishers
                             Percent of 1992 Market
   40% t


   35%.


   30%-


   25%


   20%


   15%


   10%


    5% -.
    0%
              •§
                   £
                   o
I
s
1
     Spttrce:  Surface F*>"!>"'"g Market Resenrrh Board. Metal Finishing Industry Market Survey 1992-19~
                        NOTE: Data includes both job and captive shops.

             The sale of metal  finishing services is also essentially a derived
             demand (i.e.,  sales depend entirely upon the  production of other
             industries).   However, sales by the metal finishing industry have
             not kept up with sales of the industries served.
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             In the last several years, many U.S. fastener (nuts, screws, bolts,
             rivets)  companies have become more competitive in  the  global
             market by incorporating new technology into production lines to
             improve efficiency and  quality.  In 1993, U.S. exports of industrial
             fasteners edged up about 0.6 percent; Canada and Mexico were the
             largest importers. U.S. imports of industrial fasteners also increased
             11 percent over the last several years.  This is because demand in the
             U.S. out-paced production.  The expansion of the U.S. automotive
             and residential  construction sectors was  a major factor in  the
             increase in fastener imports.

             Exports of U.S. valve and pipe fittings are  also expected to grow.
             1993  industry exports increased  six  percent compared with 1992
             figures.  Although Canada  remains the principal foreign market,
             exports to Chile  and the Philippines almost tripled,  and exports to
             developing countries increased dramatically.
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JR.   INDUSTRIAL PROCESS DESCRIPTION

            This section describes  the major industrial processes within the
            Fabricated Metal Products industry, including the materials and
            equipment  used and the  processes employed.   The  section  is
            designed for those interested in gaining a general understanding  of
            the industry, and  for  those interested  in  the inter-relationship
            between  the industrial process  and  the topics  described  in
            subsequent sections of this profile:  pollutant outputs, pollution
            prevention  opportunities, and Federal regulations.   This section
            does not  attempt to replicate published engineering information
            that is available for this industry.  Refer  to Section IX for a list  of
            reference documents that are available.

            Specifically, this section contains a description of commonly used
            production processes, the associated raw  materials, the byproducts
            produced  or released,  and  the  materials  either  recycled  or
            transferred off-site.   This  discussion,  coupled  with  schematic
            drawings  of the identified processes, provides a concise description
            of where wastes may be produced in the process.  This section also
            describes the potential fate (air, water, land) of these waste products.
III.A. Industrial Processes in the Fabricated Metal Products Industry

            In view of the high cost of most new equipment and the relatively
            long lead time necessary to bring new equipment into operation,
            changes in production methods  and products are  made only
            gradually; even new  process technologies that fundamentally
            change the industry are only adopted over long periods of time.  In
            addition, the  recent financial performance of the Fabricated Metal
            Products industry combined with the difficulty of raising funds in
            the bond market, have left many  establishments with a  limited
            ability to raise the capital necessary to purchase new equipment.

            For the purposes of this profile, the industrial processes associated
            with the Fabricated Metal Products industry will be grouped into
            three categories: fabricated metal products; surface preparation; and
            metal finishing.  Each category is discussed in greater depth in the
            following subsections.
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Fabricated. Metal Products
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HI.A.I.      Fabricated Metal Products

            Once molten metal (ferrous or nonferrous)  containing the correct
            metallurgical properties has been  produced (see  SIC 33,  which
            comprises  activities associated  with  the  nonferrous  metals
            industry), it is cast  into a form that can enter various shaping
            processes.  Recently, manufacturers have been using continuous
            casting techniques that allow the molten metal to be formed directly
            into sheets, eliminating interim forming  stages.   This  section
            identifies some of the many forming and shaping methods used by
            the metal fabrication industry.  In general, the metal may be heat
            treated or remain  cold.   Heat treating is the modification  of the
            physical properties  of  a workpiece  through  the  application  of
            controlled heating and  cooling cycles.  Cold metal is formed by
            applying direct physical pressure to the metal.

            Regardless  of the forming  method used,  the metal fabricating
            process usually employs  the use of cutting oils (e.g., ethylene glycol),
            degreasing and cleaning solvents, acids, alkalis, and heavy metals.
            The oils are typically used when forming and cutting the  metal.
            The solvents (e.g.,  trichloroethane, methyl ethyl ketone), alkalines,
            and acids (e.g., hydrochloric, sulfuric) are used to clean the surface of
            the metals.   The current trend in the  industry is to use aqueous
            non-VOCs to clean the metals, whenever possible. The use of 1,1,1-
            trichloroethane and methyl ethyl ketone is declining.

            Once molten metal is formed into a workable shape, shearing and
            forming operations are usually performed. Shearing operations cut
            materials into a desired  shape and  size, while forming operations
            bend or conform materials into specific shapes. Cutting or shearing
            operations include punching,  piercing, blanking, cutoff, parting,
            shearing, and trimming.   Basically, these operations produce holes
            or openings, or produce  blanks or parts.  The most common hole-
            making operation is  punching. Cutoff, parting, and shearing are
            similar operations with  different applications.   The rate of
            production  is  highest in hot forging operations and lowest in
            simple bending and spinning operations.

            Forming operations, as  illustrated  in Exhibit  9, shape parts by
            bending, forming,  extruding, drawing, rolling, spinning, coining,
            and forging the metal into a specific configuration.  Bending is the
            simplest forming operation;  the part  is simply bent to a specific
            angle or shape.  Other types of forming operations  produces both
            two- and three-dimensional shapes.
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Fabricated Metal Products
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                                  Exhibit 9
                            Forming Operations
                          Punch
                                              Workpiece
            Extruding is the process of forming a specific shape from a solid
            blank by forcing the blank through a die of the desired  shape.
            Extruding can produce complicated and intricate cross-sectional
            shapes.  In rolling the metal passes through a set or series of rollers
            that bend and form the part into the desired shape (See Exhibit 10).
            Coining is a process that alters the form of the part by changing its
            thickness to produce  a three-dimensional relief on one or  both sides
            of the part, like a coin.
                                  Exhibit 10
                                   Rolling
          Die Rollers
 Workpiece
             In drawing, a punch forces sheet stock into a die, where the desired
             shape is formed in the space between  the  punch  and  die.  In
             spinning, pressure is applied to the sheet while it spins on a rotating
             form, forcing the sheet to acquire the shape of the form.  Forging
             operations produce a specific shape by applying external pressure
             that  either strikes or  squeezes  a heated blank into a  die of the
             desired shape. Forging operations may be conducted on hot or cold
             metal using either single- or multi-stage dies.

             Once shearing and forming activities are complete, the  material is
             machined.   Machining refines the  shape  of a workpiece  by
 SIC Code 34
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             removing material from pieces of raw stock with machine tools.
             The  principal processes  involved in  machining  are drilling,
             milling, turning, shaping/planing, broaching^ sawing, and grinding.
III.A.2.       Surface Preparation

             The surface of the metal may require preparation prior to applying a
             finish.   Surface  preparation, cleanliness,  and  proper  chemical
             conditions are essential to ensuring that finishes perform properly.
             Without  a properly cleaned  surface, even the  most expensive
             coatings  will  fail  to  adhere or  prevent  corrosion.   Surface
             preparation techniques range from simple abrasive blasting to acid
             washes to complex, multi-stage chemical cleaning processes.  Exhibit
             11  provides a flow  chart of a representative process  used when
             preparing metal for electroplating.  Various surface preparation
             methods are discussed below.
                                  Exhibit 11
                 Process for Preparing Metal for Electroplating

Scale
Removal
Acid
Pickling "
-

Rinse

*

1
Alkaline
Cleaning
S
a
urface
eaning

Rinse

-
1
Alkaline
Cleaning

-^ Rinse

  Source: Metals Handbook, Ninth Edition: Volume 5, Surface Cleaning. Finishing, and Coating. 1982, American
                                Society for Metals.

             Some cleaning  techniques  involve  the  application  of organic
             solvents to degrease the surface of the metal.  Other  techniques,
             emulsion cleaning, for  example, use common organic solvents (e.g.,
             kerosene, mineral oil, and glycols) dispersed in an aqueous medium
             with the aid of an emulsifying agent.  Emulsion cleaning uses less
             chemical than  solvent degreasing because the  concentration of
             solvent is lower.

             Alkaline cleaning may also be utilized for the removal of organic
             soils.   Most  alkaline  cleaning solutions  are  comprised of three
             major types of components:  (1) builders, such as alkali hydroxides
             and carbonates, which make up the  largest portion of the cleaner; (2)
             organic or inorganic additives, which promote better cleaning or act
             to  affect the metal surface  in some way; and (3)  surfactants.
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            Alkaline cleaning is often assisted by mechanical action, ultrasonics,
            or by electrical potential (e.g., electrolytic cleaning).

            Acid cleaning, or pickling, can also be used to prepare the surface of
            metal  products by chemically removing oxides and scale from  the
            surface of title metal. For instance, most carbon steel is pickled with
            sulfuric or hydrochloric acid, while stainless  steel is pickled with
            hydrochloric or hydrofluoric acids, although hydrochloric acid may
            embrittle  certain types  of steel and is rarely  used.  The metal
            generally passes from the  pickling bath through a series  of rinses.
            Acid pickling is similar to acid cleaning, but is  usually used to
            remove the scale from semi-finished mill products, whereas acid
            cleaning is usually used  for near-final preparation  of metal surfaces
            before electroplating, painting, and other finishing processes.

in.A.3.      Metal Finishing

            Surface  finishing  usually involves  a  combination of metal
            deposition  operations and numerous finishing  operations.   A
            diagram depicting  the general metal finishing  process, including
            surface preparation, is provided in Exhibit 12.   Wastes typically
            generated during these operations are associated with the solvents
            and cleansers applied to the surface and the metal-ion-bearing
            aqueous solutions  used in the plating tanks.  Metal-ion-bearing
            solutions  are commonly  based on hexavalent chrome, trivalent
            chrome, copper, gold, silver,  cadmium, zinc, and nickel.  Many
            other  metals and alloys are also used, although less frequently.  The
            cleaners (e.g., acids) may appear in process wastewater; the solvents
            may be emitted into the air, released in wastewater, or disposed of
            in  solid form; and other  wastes,  including paints, metal-bearing
            sludges, and still bottom wastes, may be generated in solid form.
            Several of the many metal finishing operations are  described below.
                                   Exhibit 12
                    Overview of the Metal Finishing Process

Alkaline
Cleaner

->

Rinse

*

Acid Dip
'
Rinse

1
Surface
Preparation
-
Plating
-
Drag-out
Tanks
"*
Rinse
-
Finishing
Treatment

-»
Rinse

1
Surface
Treatment

      Source: Sustainable Industrie Promoting Strategic Environmental
                        Phase 1 Report, U.S. EPA, OERR, June 1994.
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Anodizing
            Anodizing  is an  electrolytic process  which  converts the metal
            surface to an insoluble oxide coating.  Anodized coatings provide
            corrosion protection, decorative surfaces, a base for painting and
            other  coating processes, and special electrical and  mechanical
            properties.  Aluminum is the most frequently anodized material.
            Common aluminum anodizing processes include:   chromic  acid
            anodizing, sulfuric  acid anodizing, and boric-sulfuric anodizing.
            The sulfuric acid process is the most common method.

            Following anodizing, parts  are  typically rinsed, then  proceed
            through a sealing  operation that improves the corrosion resistance
            of the coating.   Common sealants include chromic acid, nickel
            acetate, nickel-cobalt acetate, and hot water.
Chemical  Conversion Coating
            Chemical conversion coating includes chromating, phosphating,
            metal coloring, and passivating operations.  Chromate conversion
            coatings  are produced  on various metals  by  chemical  or
            electrochemical   treatment.    Solutions,  usually  containing
            hexavalent chromium and other compounds, react with the metal
            surface to form a layer containing a complex mixture of compounds
            consisting of chromium, other constituents,  and  base metal.
            Phosphate coatings may be formed by the immersion of steel, iron,
            or  zinc-plated  steel in  a dilute solution of  phosphate salts,
            phosphoric acid, and other reagents  to condition the surfaces  for
            further processing.  They are used to provide a good base for paints
            and other organic  coatings, to condition the surfaces for cold
            forming operations by providing a base for drawing compounds and
            lubricants, and to impart corrosion resistance to the metal surface.

            Metal coloring involves chemically converting the metal  surface
            into an oxide or similar metallic  compound to produce a decorative
            finish such as a green or blue patina on copper or steel, respectively.
            Passivating is the process of forming a protective film on metals by
            immersion into an acid solution, usually nitric acid or nitric acid
            with  sodium dichromate.  Stainless steel products are often
            passivated to prevent corrosion and extend the life of the product.
Electroplating
            Electroplating is the production of a surface coating of one metal
            upon another by electrodeposition.  Electroplating activities involve
            applying predominantly inorganic coatings onto surfaces to provide
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Fabricated Metal Products
                   Sector Notebook Project
            corrosion resistance,  hardness, wear  resistance, anti-frictional
            characteristics, electrical  or  thermal conductivity, or decoration.
            Exhibit 13 illustrates the important parts of typical electroplating
            equipment.  The most commonly electroplated  metals and alloys
            include:  brass (copper-zinc), cadmium, chromium, copper, gold,
            nickel, silver, tin, and zinc.

            In  electroplating, metal ions in either acid,  alkaline, or neutral
            solutions are reduced on  the workpieces being plated.  The metal
            ions in the solution are usually replenished by  the dissolution of
            metal from solid metal anodes fabricated of the same metal being
            plated, or by direct replenishment of the solution  with metal salts or
            oxides.   Cyanide, usually in the form of sodium or potassium
            cyanide,  is usually used as a complexing agent for cadmium and
            precious  metals electroplating, and  to  a lesser degree, for other
            solutions such as copper and zinc baths.
                                  Exhibit 13
                       Typical Electroplating Equipment
        Generator or
          Rectifier
               4-
         Voltmeter
                \
                                                        Anode Bus Bar
                                                         Cathode Bus Bar
            Source: McGraw Hill Encyclopedia of Science and lechnolow. Volume b.
             The sequence of steps in an electroplating includes: cleaning, often
             using alkaline and acid solutions; stripping of old plating or paint;
             electroplating;  and  rinsing between  and  after each  of these
             operations.  Sealing and  conversion coating may be  employed on
             the metals after electroplating operations.
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Electroless Plating
             Electroless plating is the chemical deposition of a metal coating onto
             a plastic object, by immersion of the object in a plating solution.
             Copper and nickel electroless plating is commonly used for printed
             circuit boards.   The basic  ingredients  in an electroless  plating
             solution are:   a source  of metal (usually  a  salt);  a reducer; a
             complexing agent to hold the metal in solution; and various buffers
             and other chemicals designed to maintain bath stability and increase
             bath life.   Immersion plating produces a  thin  metal  deposit,
             commonly zinc  or  silver, by chemical  displacement.  Immersion
             plating baths are usually formulations of  metal salts, alkalis, and
             complexing agents (e.g., lactic, glycolic, malic acid salts).  Electroless
             plating and immersion plating commonly generate more waste
             than other  plating  techniques,  but individual  facilities vary
             significantly in efficiency.  Exhibit 13 illustrates a typical plating
             process.
                                    Exhibit 14
                            Electroless Plating Process
          Drag-out
       Drag-out
       Drag-out
      Drag-out
      Drag-out
     Plate
     Tanks
Recovery
  Rinse
Neutralizer
                                             I
 Cold
Water
                                      Spent
                                    Solution

 Hot
Water
                                       Rinse
                                       Water
                                                      I
 Other
Processes
                                                           Discharge
  Source: Pollution Prevention and Control Technology for Plating Operations, First Edition, National Center for
              Manufacturing Sciences and National Association of Metal Finishers, 1994.
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Painting
            Painting  involves  the application  of  predominantly  organic
            coatings to a workpiece for protective and/or decorative purposes.
            It is  applied in various forms, including dry powder,  solvent-
            diluted formulations,  and  water-borne formulations.   Various
            methods of application are used,  the most common being spray
            painting and electrodeposition.  Spray painting is a process by which
            paint is placed into a pressurized cup or pot and is atomized into a
            spray pattern when it is released from the vessel and forced through
            an orifice. Electrodeposition is the process of coating a workpiece by
            either making  it anodic or cathodic in a bath that  is generally an
            aqueous emulsion of the coating material.  When applying the
            paint as a dry powder,  some form of heating or baking is necessary
            to ensure that the powder adheres to the metal. These processes
            may  result  in solvent  waste (and associated still  bottom wastes
            generated during solvent  distillation), paint sludge wastes, paint-
            bearing wastewaters, and paint solvent emissions.
Other  Metal Finishing  Techniques
            Polishing, hot dip coating, and etching are processes that are also
            used to finish metal.  Polishing is an abrading operation used to
            remove or smooth out surface defects (scratches, pits, or tool marks)
            that adversely affect the appearance or function of a part. Following
            polishing operations, area cleaning  and washdown can produce
            metal-bearing wastewaters.  Hot dip coating is the coating of a
            metallic workpiece with another metal to provide a protective film
            by immersion into a molten bath.  Galvanizing  (hot dip zinc) is a
            common form  of hot  dip coating.  Water is used  for  rinses
            following precleaning and sometimes for quenching after coating.
            Wastewaters  generated  by these operations  often contain metals.
            Etching produces specific designs or surface appearances on parts by
            controlled dissolution with chemical  reagents or etchants. Etching
            solutions commonly comprise strong acids or bases with  spent
            etchants containing high concentrations of spent metal.   The
            solutions include ferric chloride, nitric acid,  ammonium persulfate,
            chromic acid, cupric chloride, and hydrochloric acid.
 SIC Code 34
                                       20
       September 1995

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Fabricated Metal Products
                                                            Sector Notebook Project
III.B.  Raw Material Inputs and Pollution Outputs in the Production Line

             The  material inputs and pollution outputs resulting from metal
             fabrication, surface  preparation, and metal finishing processes are
             presented by media in Exhibit 15.  Exhibit 16 illustrates the general
             processes associated with this industry,  the pollutants generated,
             and the point in the process at which the pollutants are produced.
September 1995
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Fabricated Metal Products
Sector Notebook Project
                                    Exhibit 15
                       Process Materials Inputs and Outputs
Bll
Material Input || Air Emission
Process
Wastewater
Solid Waste
Metal Shaping
Metal Cutting and/or
'orming
Cutting oils,
degreasing and
cleaning solvents,
acids, alkalis, and
heavy metals
Solvent wastes
(e.g., 1,1,1-
trichloroethane,
acetone, xylene,
toluene, etc. )
Waste oils (e.g.,
ethylene glycol)
and acid (e.g.,
hydrochloric,
sulfuric, nitric),
alkaline, and
solvent wastes
Surface Preparation
Solvent Degreasing
and Emulsion,
Alkaline, and Acid
Cleaning
Solvents, emulsifying
agents, alkalis, and
acids
Solvents
(associated with
solvent
degreasing and
emulsion cleaning
only)
Solvent,
alkaline, and
acid wastes
Surface Finishing
Anodizing
Chemical Conversion
Coating
Electroplating
Plating
Painting
Other Metal
Finishing Techniques
(Including Polishing,
Hot Dip Coating, and
Acids
Metals and acids
Acid/ alkaline
solutions, heavy
metal bearing
solutions, and cyanide
bearing solutions
Metals (e.g., salts),
complexing agents,
and alkalis
Solvents and paints
Metals and acids
Metal-ion-
bearing mists and
acid mists
Metal-ion-
bearing mists and
acid mists
Metal-ion-
bearing mists and
acid mists
Metal-ion-
bearing mists
Solvents
Metal fumes and
acid fumes
Acid wastes
Metal salts, acid,
and base wastes
Acid /alkaline,
cyanide, and
metal wastes
Cyanide and
metal wastes
Solvent wastes
Metal and acid
wastes
Metal chips (e.g.,
scrap steel and
aluminum),
metal-bearing
cutting fluid
sludges, and
solvent still-
bottom wastes

Ignitable wastes,
solvent wastes,
and still bottoms

Spent solutions,
wastewater
treatment
sludges, and base
metals
Spent solutions,
wastewater
treatment
sludges, and base
metals
Metal and
reactive wastes
Cyanide and
metal wastes
Still bottoms,
sludges, paint
solvents, and
metals
Polishing sludges,
hot dip tank
dross, and etching
sludges
 SIC Code 34
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        September 1995

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Fabricated Metal Products
                                                                     Sector Notebook Project
Exhibit 16
Fabricated Metal Products Manufacturing Processes

Metal
Fabrication
Metal
Preparation
(Cleaning)
Emulsifyui
Agents
Metal
Finishit
Cyai
Acids
X
Metals^
Alkalin
Metals
*s
-^ i
Anodizing — ^
Rinsing ^^
* ^<
Sealing
Tides
^"^ \
Electroplating — Q
1 * ^
Rinsing -^^^
t C
Scaling and/or
Conversion Coating
* *x
Rinsing ^^^
Molten
Metal 	 ^^^
Metal
and/or
Pro
Cutting
cess
Rinsing and Bathing'
Alkalines Operations s
Acids
^•^ Metal
g.^, Qeaning
	 _ Rinsing ai
Oper

Air Emiss to us}

^Wg>
So U$ Wastes*}


^n&J^*}

**— - _ 	 — "^
Jz0w^?>

Waste MSifef ^
Solid' Wastes*}

'4
nd Bathing _
at ions
Metals.^


Metals^
Gomplexing
Agents

^^ocntotete*}

•^ f"

crnpMetaZ^^

^.^-—(''viiaste. Waia**^)
~—~~~i^ ^>*^. ' - , 	 ^
— — — _
- ^x2
- — — — — _
3C£m^^
, 	
-^ ^
^^^^^1
^•masfeT)

^^^^.(^teW^*}

^^ i r
Chemical
Conversion
Coating
Rinsing ^^^
Acids
^^
^C^ Waste Water J
***(^SolitI Wastes*}
L Alkalis
Plating
{
Rinsing ^^_

—C^SM^T^

— <^^W^>

Solvents i Paints
^^T-*--^ 	


t Acids
^*-
Other Metal
Finishing
Tediniques
Rinsing 	 ^Tl

Waste Water ^}

Painting
Rinsing _
^(^Aa-Bm-ssm^}

^*^^id Wastes*}

—f*^' ^



September 1995
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Fabricated Metal Products
Sector Notebook Project
III.B.l.      Metal Fabrication

            Each of the metal shaping processes can result in wastes containing
            chemicals of concern.  For example, the application of solvents to
            metal  and machinery results  in air emissions.  Additionally,
            wastewater containing acidic or  alkaline wastes and waste oils, and
            solid wastes, such as  metals and solvents, are usually generated
            during this process.

            Metal fabrication  facilities are  major  users  of  solvents  for
            degreasing.  In cases where  solvents are used solely in degreasing
            (not used in  any other plant  operations), records of the amount and
            frequency of purchases provide  enough  information  to estimate
            emission rates, based on the assumption that  all solvent purchased
            is eventually emitted.  Section V.D., Pollution Prevention Options,
            illustrates techniques that may be used to reduce the loss of solvents
            to the atmosphere.

            Metalworking fluids are applied to either the tool or the metal being
            tooled to facilitate the shaping operation. Metalworking  fluid is
            used to:

            •     Control and reduce the  temperature  of tools and  aid
                  lubrication,

            •     Control and reduce the temperature of workpieces and aid
                  lubrication,

            •     Provide a good finish,

            •     Wash away chips and  metal debris, and

            •     Inhibit corrosion or surface oxidation.


            Fluids  resulting from this  process typically become  spoiled or
            contaminated with extended use and reuse.   In general, metal
            working  fluids  can be petroleum-based, oil-water emulsions,  and
            synthetic  emulsions.  When disposed, these fluids may  contain
            high levels of  metals  (e.g.,  iron, aluminum, and copper).
            Additional  contaminants  present in fluids  resulting from these
            processes include acids and alkalis  (e.g., hydrochloric, sulfuric,
            nitric), waste oils, and solvent wastes.

            Scrap metal may  consist of  metal removed from  the original piece
            (e.g.,  steel), and  may be combined with  small  amounts of
            metalworking fluids (e.g., solvents) used prior to and during the
 SIC Code 34
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Fabricated Metal Products
                                                           Sector Notebook Project
             metal shaping operation that generates the scrap.  Quite often, this
             scrap is reintroduced into the process as a feedstock. The scrap and
             metalworking fluids, however, should be tracked since they may be
             regulated as solid wastes.

III.B.2.       Surface Preparation

             Surface preparation  activities  usually result in  air emissions,
             contaminated wastewater,  and  solid wastes.   The  primary  air
             emissions from cleaning are due to the evaporation of chemicals
             from solvent degreasing and emulsion cleaning processes.  These
             emissions may result through  volatilization of  solvents during
             storage, fugitive losses during use, and direct ventilation of fumes.

             Wastewaters  generated from cleaning are primarily rinse waters,
             which are usually combined with other metal finishing wastewaters
             (e.g., electroplating) and treated  on-site by conventional hydroxide
             precipitation. Solid wastes (e.g.,  wastewater treatment sludges, still
             bottoms, cleaning tank residues, machining fluid residues, etc.) may
             also be generated by  the cleaning operations. For  example, solid
             wastes are generated when cleaning solutions become ineffective
             and are replaced. Solvent-bearing wastes are typically pre-treated to
             comply with any applicable National  Pollutant Discharge System
             (NPDES) permits and  then sent off-site, while aqueous wastes from
             alkaline and acid cleaning , which do not contain solvents, are often
             treated on-site.

III.B.3.       Metal Finishing

             Many metal finishing operations are typically performed  in baths
             (tanks) and are then followed by rinsing cycles. Exhibit 17 illustrates
             a  typical  chemical or electrochemical process step  in which a
             workpiece enters the process bath containing process chemicals that
             are carried to the rinse water (drag-out).  Metal plating and related
             waste account for  the largest volumes of metal- (e.g.,  cadmium,
             chromium, copper,  lead, and nickel) and cyanide-bearing wastes.
             Painting operations account for  the generation of solvent-bearing
             wastes and the direct release of solvents (including benzene, methyl
             ethyl ketone, methyl isobutyl ketone, toluene, and xylene). Paint
             cleanup operations may contribute to the release  of chlorinated
             solvents (including carbon tetrachloride, methylene chloride, 1,1,1-
             trichloroethane, and perchloroethylene).  Compliance with one law
             through emission or effluent controls may generate waste regulated
             under another statute  (e.g., effluent controls required by the Clean
             Water  Act may generate  sludges  which  are  regulated  by the
September 1995
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Fabricated Metal Products
                                         Sector Notebook Project
            Resource Conservation and Recovery Act).   The  nature of the
            wastes produced by these processes is discussed further below.
                                  Exhibit 17
                     Typical Metal Finishing Process Step
      Workplace
Vapors/Mist


     I          Workpiece
     Process
    Chemicals
                   Process
                    Bath
                    T
Workpiece To Next Step
                               Rinse
                               System
                                          Wastewater
                  Spent Bath      Fresh Water
                   (Waste)
     Source: Guides to Pollution Prevention:  The Metal Finishing Industry. U.S. EPA, ORD, October 1992.
Anodizing
             Anodizing  operations  produce  air  emissions,  contaminated
             wastewaters, and solid wastes.  Mists and gas bubbles arising from
             heated fluids  are a source of air  emissions, which may contain
             metals or other substances present in the bath.  When dyeing of
             anodized coatings occurs, wastewaters produced may contain nickel
             acetate, non-nickel sealers, or substitutes  from  the  dye.   Other
             potential pollutants include complexers and metals  from dyes and
             sealers.   Wastewaters  generated from anodizing  are usually
             combined with other metal finishing wastewaters and treated  on-
             site  by  conventional  hydroxide precipitation.   Wastewaters
             containing chromium must be pretreated to  reduce hexavalent
             chromium to  its trivalent  state.    The conventional treatment
             process generates a sludge that is  usually  sent off-site for metals
             reclamation and/or disposal.

             Solid wastes generated from anodizing include spent solutions and
             wastewater treatment sludges.   Anodizing  solutions  may  be
             contaminated with the base metal being processed  due  to the anodic
             nature  of the  process.   These  solutions eventually  reach  an
             intolerable concentration of dissolved metal and require processing
 SIC Code 34
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Fabricated Metal Products
                                                         Sector Notebook Project
             to  remove the  dissolved  metal  to  a  tolerable  level  or
             treatment/disposal.

Chemical Conversion Coating

             Chemical  conversion coating generally produces contaminated
             wastewaters and  solid waste.  Pollutants associated with these
             processes  enter the  wastestream through rinsing and  batch
             dumping of process baths. The process baths usually contain metal
             salts, acids, bases, and dissolved basis  materials.  Wastewaters
             containing chromium are usually  pretreated to reduce hexavalent
             chromium  to  its trivalent  state.  The conventional  treatment
             process generates a sludge that is sent off-site for metals reclamation
             and/or disposal.  Solid  wastes  generated from these  processes
             include  spent  solutions and wastewater  treatment  sludges.
             Conversion coating solutions may also be contaminated with the
             base metal being processed.  These solutions will eventually reach
             an  intolerable  concentration of  dissolved  metal  and  require
             processing to remove the dissolved metal to a tolerable level.
Electroplating
            Electroplating  operations produce  air  emissions,  contaminated
            wastewaters  and solid wastes.  Mists arising from electroplating
            fluids and process gases can be a source of air emissions, which may
            contain metals  or  other substances present in  the  bath.   The
            industry  has  recently  begun  adding  fume  suppressants  to
            electroplating baths to reduce air emissions of chromium, one of
            the most frequently electroplated metals.  The fume suppressants
            lower the surface tension of the bath, which prevents hydrogen
            bubbles in the bath  from bursting and producing a  chromium-laden
            mist.  The fume suppressants are highly effective when used in
            decorative plating, but less effective when used in hard-chromium
            plating.  Contaminated wastewaters result from  workpiece rinsing
            and process cleanup waters.  Rinse waters from electroplating are
            usually combined  with  other  metal finishing  wastewaters and
            treated  on-site by  conventional  hydroxide   precipitation.
            Wastewaters  containing chromium must be pretreated to reduce
            hexavalent chromium to its trivalent  state.  These  wastewater
            treatment  techniques  can  result  in  solid-phase wastewater
            treatment sludges.   Other wastes generated from  electroplating
            include spent solutions which become contaminated during use,
            and therefore, diminish performance of the process.  In addition to
            these wastes, spent process solutions and quench bathes may be
            discarded periodically when the concentrations of contaminants
            inhibit proper function of the solution or bath.
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Fabricated Metal Products
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Electroless  Plating
Painting
            Electroless plating produces contaminated wastewater  and solid
            wastes.  The spent plating solution and rinse water are usually
            treated chemically to precipitate out the toxic metals and  to destroy
            the cyanide.  Electroless plating solutions can be difficult to treat;
            settling  and  simple chemical  precipitation are not effective at
            removing the chelated metals used in the plating bath.  The extent
            to which plating solution carry-over  adds to  the wastewater  and
            enters the sludge depends on the type of article being plated and the
            specific  plating method employed.  However, most  sludges may
            contain  significant concentrations of toxic metals, and may  also
            contain complex cyanides in high concentrations if cyanides are not
            properly isolated during the treatment process.
             Painting operations result in emissions, contaminated wastewaters,
             and the  generation of liquid and solid wastes.   Atmospheric
             emissions consist primarily of the organic solvents used as carriers
             for the paint.   Emissions also result from paint storage, mixing,
             application, and drying. In addition, cleanup processes can result in
             the  release  of organic solvents used to  clean  equipment  and
             painting  areas.  Wastewaters are often generated  from painting
             processes due primarily to the discharge of water from water curtain
             booths.   On-site  treatment processes  to  treat  contaminated
             wastewater  generate a sludge that is sent off-site for  disposal.
             Sources of solid- and liquid-phase wastes include:

             •     Paint  application emissions control devices (e.g., paint booth
                   collection systems, ventilation filters, etc.)

             •     Equipment washing

             •     Disposal materials used to contain paint and overspray

             •     Excess  paints  discarded upon  completion  of a painting
                   operation or after expiration of the paint shelf-life.


             These  solid and liquid wastes may contain metals from paint
             pigments and  organic solvents, such as paint solvents and cleaning
             solvents.  Still bottoms also contain solvent wastes.  The cleaning
             solvents  used on painting equipment and  spray booths may also
             contribute organic solid  waste to the wastes removed from the
             painting  areas.
 SIC Code 34
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       September 1995

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Fabricated Metal Products
                                                         Sector Notebook Project
Other Metal  Finishing Techniques
            Wastewaters are  often  generated during  other metal finishing
            processes.  For  example, following  polishing operations,  area
            cleaning and washdown can produce metal-bearing wastewaters.
            Hot dip coating techniques, such as galvanizing, use water for rinses
            following pre-cleaning and sometimes for quenching after coating.
            Hot dip  coatings also generate solid waste, anoxide  dross,  that is
            periodically  skimmed  off the  heated tank.   These  operations
            generate  metal-bearing  wastewaters.   Etching solutions  are
            comprised of  strong  acids  (e.g.,  ferric  chloride, nitric acid,
            ammonium persulfate) or bases.  Resulting spent etchant solutions
            may contain metals and acids.
III.C.  Management of Chemicals in Wastestream

            The Pollution Prevention Act of 1990 (EPA) requires facilities to
            report information about  the  management of TRI chemicals in
            waste and  efforts made to eliminate or reduce those quantities.
            These data have been collected annually in Section 8 of the TRI
            reporting Form R beginning with the 1991 reporting year. The data
            summarized  below  cover  the  years 1992-1995 and  is meant to
            provide a basic understanding of the quantities of waste handled by
            the industry,  the methods typically used to  manage this waste, and
            recent trends  in these methods.  TRI waste management data can be
            used  to assess trends  in  source reduction  within  individual
            industries  and facilities, and  for  specific TRI chemicals.  This
            information  could  then  be  used  as a  tool  in   identifying
            opportunities for pollution prevention  compliance  assistance
            activities.

            While the quantities reported for  1992  and 1993 are estimates of
            quantities already managed,  the quantities reported for 1994 and
            1995 are projections  only.  The EPA requires these projections to
            encourage facilities to consider  future waste generation and source
            reduction of  those quantities as well as movement up the waste
            management  hierarchy.    Future-year  estimates  are  not
            commitments that facilities reporting under TRI  are  required to
            meet.

            Exhibit 18 shows that the fabricated metals industry managed about
            798 million pounds of production-related waste (total quantity of
            TRI chemicals in the waste from routine production operations) in
            1993 (column B).  Column C reveals that of this production-related
September 1995
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Fabricated Metal Products
Sector Notebook Project
            waste, 34 percent was either transferred off-site or released to the
            environment.  Column  C is calculated by dividing  the total TRI
            transfers and releases by the total quantity  of production-related
            waste. In other words, about 62 percent of the industry's TRI wastes
            were managed  on-site through recycling,  energy  recovery, or
            treatment  as shown in columns D, E and  F, respectively.  The
            majority of  waste that  is released or transferred off-site can be
            divided into portions that are recycled off-site, recovered for energy
            off-site,  or treated off-site as shown in columns G, H,  and I,
            respectively.  The remaining portion of the production-related
            wastes (13.2 percent), shown in column J, is either released to the
            environment through direct discharges  to  air,  land,  water, and
            underground injection, or it is disposed off-site.

            From the yearly data presented below it is apparent that the portion
            of TRI wastes reported  as recycled on-site is projected  to  decrease
            and the portions treated or  managed through energy recovery on-
            site have increased between 1992 and 1995 (projected).
                                  Exhibit 18
              Source Reduction and Recycling Activity for SIC 34
A
Year
1992
1993
1994
1995
B
Production
Related
Waste
Volume
(106lbs.)*
750
798
735
697
C
% Reported
as Released
and
Transferred
38%
34%
—
—
D
E
F
On-Site
%
Recycled
23.22%
26.48%
27.91%
19.20%
% Energy
Recovery
12.24%
11.04%
8.90%
13.86%
%
Treated
23.11%
24.24%
26.33%
27.78%
G
H
I
Off-Site
%
Recycled

21.31%
22.18%
23.94%
% Energy
Recovery

1.54%
1.53%
1.63%
%
Treated

2.10%
2.32%
2.46%
J
Remaining
Releases
and
Disposal

13.28%
10.84%
11.13%
 SIC Code 34
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       September 1995

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Fabricated Metal Products
                                                          Sector Notebook Project
IV.   CHEMICAL RELEASE AND TRANSFER PROFILE

            This section is designed to provide background information on the
            pollutant releases that are reported by this industry. The best source
            of comparative pollutant  release information is the Toxic Release
            Inventory System (TRI).  Pursuant to the Emergency Planning and
            Community Right-to-Know Act, TRI includes self-reported facility
            release and transfer data for over 600 toxic chemicals.  Facilities
            within SIC Codes 20-39 (manufacturing industries) that have more
            than  10 employees, and  that are above weight-based reporting
            thresholds are required to report TRI on-site releases and off-site
            transfers.  The information presented within the sector notebooks is
            derived from the most recently available (1993) TRI reporting year
            (which then included 316 chemicals), and focuses  primarily on the
            on-site releases reported by each sector.  Because TRI requires
            consistent reporting regardless of sector, it  is an excellent tool for
            drawing comparisons across industries.

            Although  this  sector notebook  does  not  present  historical
            information regarding TRI chemical releases over time, please note
            that in general, toxic chemical releases have been declining. In  fact,
            according to the 1993 Toxic Release Inventory Data Book, reported
            releases dropped by 42.7 percent between 1988 and 1993. Although
            on-site releases have decreased, the total amount of reported toxic
            waste has not declined because  the amount of toxic  chemicals
            transferred off-site has increased.  Transfers have increased from 3.7
            billion pounds in  1991 to  4.7 billion pounds in 1993.   Better
            management practices have led to increases in off-site transfers of
            toxic  chemicals for recycling.  More detailed  information can be
            obtained from EPA's annual  Toxics Release Inventory Public Data
            Release book (which is available through the EPCRA Hotline at 1-
            800-535-0202), or directly from the Toxic Release Inventory System
            database (for user support call 202-260-1531).

            Wherever possible, the sector notebooks present  TRI data as the
            primary  indicator  of chemical  release within  each  industrial
            category.  TRI data provide the type, amount, and media receptor of
            each  chemical  released or transferred.  When other  sources of
            pollutant  release  data have  been obtained, these data have been
            included to augment the TRI information.

TRI Data Limitations

            The  reader  should keep in  mind the  following limitations
            regarding TRI data. Within  some sectors, the majority  of facilities
            are not subject to TRI reporting because they are not  considered
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Fabricated Metal Products
Sector Notebook Project
            manufacturing industries, or because they are below TRI reporting
            thresholds.  Examples are the mining, dry cleaning, printing, and
            transportation equipment cleaning sectors.  For these sectors, release
            information from other sources has been included.

            The reader should also be aware that TRI "pounds released" data
            presented within  the notebooks is  not equivalent  to a  "risk"
            ranking for each industry.  Weighting each pound of release equally
            does not factor in the relative  toxicity  of  each chemical that is
            released.  The Agency is in the process of developing an approach to
            assign toxicological weightings to each chemical released so that one
            can differentiate between pollutants with significant differences in
            toxicity.  As a preliminary indicator of the environmental impact of
            the industry's most  commonly  released chemicals, the notebook
            briefly summarizes  the toxicological properties  of the top five
            chemicals (by weight) reported by each industry.

Definitions Associated With Section IV Data Tables

General Definitions

            SIC Code — the Standard Industrial Classification (SIC) is a statistical
            classification standard used for all  establishment-based  Federal
            economic statistics.   The SIC codes facilitate comparisons between
            facility and industry data.

            TRI Facilities — are manufacturing facilities that have 10 or more
            full-time employees and are  above established chemical throughput
            thresholds.  Manufacturing facilities are defined as  facilities in
            Standard Industrial Classification primary codes 20-39. Facilities
            must  submit estimates for  all  chemicals that  are  on the  EPA's
            defined list and are above throughput thresholds.

Data Table Column Heading Definitions

            The following definitions  are based upon standard definitions
            developed  by EPA's Toxic  Release Inventory  Program.   The
            categories below represent the possible pollutant destinations that
            can be reported.                                        :

            RELEASES — are an on-site discharge  of a toxic chemical  to the
            environment.  This  includes emissions to the air, discharges to
            bodies of water, releases at the facility to land, as well  as contained
            disposal into underground injection wells.
 SIC Code 34
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Fabricated Metal Products
                                                          Sector Notebook Project
            Releases to Air (Point and Fugitive Air Emissions) — Include all air
            emissions from industry activity.  Point emissions occur through
            confined air streams as found in stacks, ducts, or pipes.  Fugitive
            emissions  include losses  from equipment  leaks, or evaporative
            losses from impoundments, spills, or leaks.

            Releases to Water (Surface Water Discharges) - encompass any
            releases going directly to streams, rivers, lakes, oceans,  or other
            bodies of water.  Any estimates for stormwater runoff and non-
            point losses must also be included.

            Releases to Land — includes disposal of waste to on-site  landfills,
            waste  that is land  treated or incorporated into soil,  surface
            impoundments, spills, leaks, or waste piles.  These activities must
            occur within the facility's boundaries for inclusion in this category.

            Underground Injection — is a contained release of a fluid into a
            subsurface well for the purpose of waste disposal.

            TRANSFERS— is a transfer of toxic chemicals in wastes to  a facility
            that is  geographically or physically separate from  the facility
            reporting  under  TRI.   The quantities reported  represent  a
            movement  of the chemical away from the reporting facility. Except
            for off-site  transfers for disposal, these quantities do not necessarily
            represent entry of the chemical into the environment.

            Transfers to POTWs — are wastewaters transferred through pipes or
            sewers to a publicly owned treatments works (POTW).  Treatment
            and chemical removal  depend  on the  chemical's nature  and
            treatment methods used.  Chemicals not treated or destroyed by the
            POTW are  generally released to surface waters or landfilled within
            the sludge.

            Transfers  to Recycling —  are sent off-site for the purposes of
            regenerating or recovering  still valuable  materials.   Once these
            chemicals  have been recycled, they may be returned to the
            originating facility or sold commercially.

            Transfers to Energy Recovery — are wastes combusted off-site in
            industrial furnaces for energy recovery.  Treatment of a chemical by
            incineration is not  considered to be energy recovery.

            Transfers  to Treatment — are wastes moved off-site for either
            neutralization, incineration, biological destruction, or physical
            separation.   In some  cases,  the chemicals are not destroyed but
            prepared for further waste management.
September 1995
33
SIC Code 34

-------
Fabricated Metal Products
                   Sector Notebook Project
            Transfers  to Disposal — are wastes taken to another facility for
            disposal  generally  as a  release  to  land  or  as  an injection
            underground.
IV.A.       EPA Toxic Release Inventory for the Fabricated Metal Products
            Industry

            TRI release  amounts listed below are not associated with non-
            compliance with environmental laws.  These facilities appear based
            on self-reported data submitted to the Toxic Release  Inventory
            program.

            The TRI database contains a detailed compilation of self-reported,
            facility-specific  chemical releases.  The top reporting  facilities for
            this sector are listed below. Facilities that have reported only the
            SIC codes covered under this notebook appear in Exhibit 19.  Exhibit
            20 contains  additional facilities that have reported the SIC code
            covered within  this report, and one or more SIC codes that are not
            within  the scope of this notebook.  Therefore,  Exhibit 20 includes
            facilities that conduct multiple operations — some that  are under
            the scope of this notebook, and some that are not. Currently, the
            facility-level data do not allow pollutant releases to be broken apart
            by industrial process.

            Exhibits 21  - 24 illustrate the TRI releases and transfers  for the
            Fabricated Metal Products industry (SIC 34).  For the industry as a
            whole,  solvents comprise the largest number of TRI releases.  This
            reflects the  fact that solvents are used during numerous metal
            shaping, surface preparation, and surface finishing operations.  For
            example, during metal shaping and surface preparation operations,
            solvents are used primarily to degrease metal.  Solvents  are also
            used during painting operations.  All of the processes which use
            solvents  generally  result  in  air  emissions,  contaminated
            wastewater, and solid wastes.

            Between  1988 and 1993, the Fabricated Metals Products industry
            substantially reduced its TRI transfers and releases (see  section V.
            Pollution Prevention Opportunities).  Exhibits 21 and  22 show the
            differences in transfers and releases over time, categorized by type of
            transfer or release.
 SIC Code 34
34
September 1995

-------
Fabricated Metal Products
                                                                Sector Notebook Project
              Exhibit 19 lists the ten facilities with the highest total TRI releases,
              most of which are continuous coil manufacturers (e.g., facilities that
              manufacture aluminum cans from long  strips of metal).   The
              wastes generated by these  manufacturers  are  not necessarily
              representative of the wastes generated by the metal fabricating and
              finishing industries as a whole.

                                     Exhibit 19
             Top 10 TRI Releasing Fabricated Metal Products Facilities
SIC Codes
3411
3411
3710, 3714,
3465
3471
3731, 3441,
3443
3411
3411
3479
3714, 3471
3341, 3479,
3355
Total TRI
Releases in
Pounds
946,923
880,500
822,902
708,285
688,540
636,126
624,250
619,436
618,359
570,622
Facility Name
U.S. Can Co., Plant 20
Weirton
Metal Container Corp.,
NWB
CMC NAO Flint OPS., BOC
Flint Automotive Div.
Plastene Supply Co.
Ingalls Shipbuilding, Inc.
American National Can Co.,
Winston Salem Plant
Metal Container Corp. FTA
Ken-Koat, Inc.
Keeler Brass Automotive,
Kentwood Plant
Commonwealth Aluminum
Corp.
City
Weirton
New Windsor
Flint
Portageville
Pascagoula
Winston-Salem
Fort Atkinson
Huntington
Grand Rapids
Lewisport
State
WV
NY
MI
MO
MS
NC
WI
IN
MI
KY
                    Source: U.S. EPA, Toxics Release Inventory Database, 1993.

Note: Being included on  this list does not mean that the release is associated with non-compliance
      with environmental laws.
September 1995
35
SIC Code 34

-------
Fabricated Metal Products
                      Sector Notebook Project
                                       Exhibit 20
       Top 10 TRI Releasing Metal Fabricating & Finishing Facilities (SIC 34)
Rank
1
2
3
4
5
6
7
8
9
10
Total TRI
Releases in
Pounds
946,923
880,500
708,285
636,126
624,250
619,436
545,505
541,654
524,346
492,872
Facility Name
U.S. Can Co., Plant 20, Weirton
Metal Container Corp., NWB
Plastene Supply Co.
American National Can Co.,
Winston Salem Plant
Metal Container Corp.
Ken-Koat, Inc.
Metal Container Corp.
Reynolds Metals Co.
Hickory Springs Mfg. Co.
Tennessee Electroplating, Inc.
City
Weirton
New Windsor
Portageville
Winston-Salem
Fort Atkinson
Huntington
Columbus
Houston
Fort Smith
Ripley
State
WV
NY
MO
NC
WI
IN
OH
TX
AR
TN
                      Source: U.S. EPA, Toxics Release inventory Uataoase,
Note: Being included on this list does not mean that the release is associated with non-compliance
      with environmental laws.
                                       Exhibit 21
              Reductions in TRI Releases, 1988-1993 (SIC 34)
Releases
Total Air Fjnissions
Surface Water Discharges
Underground Injection
Releases to Land
1988
131,296,827
1,516,905
386,120
4,202,919
1993
90,380,667
101,928
1,490
660,072
Percent
Reduction
31.2
93.3
99.6
84.4
                      Source:  U.S. EPA, Toxics Release inventory Database,
                                       Exhibit 22
                   Reductions in TRI Transfers, 1988-1993 (SIC 34)
Transfers
Recycling
Energy
Treatment
POTWs
Disposal
Other Off-Site Transfers
1988
213,214,641
12,331,653
34,313,199
17,149,495
43,529,628
8,303,148
1993
244,278,696
13,812,271
18,561,504
3,809,715
19,736,496
369,491
Percent Reduction
-14.6
-12.0
45.9
77.8
54.7
95.5
                      Source:  U.S. EPA, Loxics Release Inventory uataoase,
 SIC Code 34
36
September 1995

-------
Fabricated Metal Products
                                                                    Sector Notebook Project
                                       Exhibit 23
      TRI Reporting Metal Fabricating & Finishing Facilities (SIC 34) by State
State
AL
AR
AS
AZ
CA
CO
CT
DE
FL
GA
ffl
IA
ID
IL
IN
KS
KY
LA
MA
MD
ME
MI
MN
MO
Number of
Facilities
54
25
1
17
208
19
83
2
36
42
2
30
1
230
111
16
41
12
76
17
5
159
59
54
State
MS
NC
NE
NH
NJ
NV
NY
OH
OK
OR
PA
PR
RI
SC
SD
TN
TX
UT
VA
WA
WI
WV
WY

Number of
Facilities
29
35
9
5
60
3
101
225
29
20
123
10
30
37
3
47
107
15
30
24
103
16
2

                     Source: U.S. EPA, Toxics Release Inventory Database, 1993.
September 1995
37
SIC Code 34

-------
Fabricated Metal Products
Sector Notebook Project
                                   Exhibit 24
 Releases for Metal Fabricating & Finishing Facilities (SIC 34) in TRI, by Number
                 of Facilities (Releases reported in pounds/year)
Chemical Nsnic
Sulluric Acid
lydrochloric Acid
•Jitric Acid
Cylcne (Mixed
Isomers)
Nickel
riiroinium
^anganese 	
Glycol Ethers
Copper 	
vlethyl Ethyl Ketone
Zinc Compounds 	
<-Butyl Alcohol
Toluene
l-Trichloroethane
Triehloroethylene
Chromium Compounds
Phosphoric Acid 	
Nickel Compounds
Vtcihyl Isobutyl Kelone
Cyanide Compounds
Copper Compounds
Lead
Ammonia
Elhylbcnzene 	
Hydrogen Fluoride
Zinc (Fume Or Dust)
Acetone
Manganese
Compounds 	
Dichloromcthanc
4-Trimethylbenzene
Tctroehloroethylene
Mcthanol 	
Chlorine 	
McthyIcncbis(Phcnylis
oeyanale) 	
Naphthalene 	
Cobalt
Barium Compounds
Ffconll3 	
Lead Compounds 	
Styrone 	
Cadmium
Formaldehyde 	
Aluminum (Fume Or
Dusrt
Trichlorofluoro-
mcthanc
Cadmium Compounds
Bthvlcnc Glycol
Propylcnc 	
Cumenc
a-Elhoxyethanol
Cyelohcxane 	
fsopropyl Alcohol
(Manufacturing
Antimony Compounds
Cobalt Compounds
M-Xylene 	
# Facilities
Reporting
Chemical
861
652
390
336
311
287
271
269
267
254
228
215
205
189
185
176
175
158
114
103
93
83
79
74
74
70
61
58
57
53
49
48
35
I 33
1 28
I 25
	 19_
19
17
16
16
13
13
11
11
11
c
	 8_
6

Fugitive
Air
186135
264628
81650
2982600
23285
25150
29884
4990228
19231
2134002
87045
3209678
1366663
2046210
2410195
7039
49587
7538
501363
7686
4912
5758
87916
234540
12924
100770
407417
2197
991302
255913
809152
64182
2562
57791
1534
3606
282200
961
62
15561
7042
45312
276
37417
25423
10383
14361
611237
22111
4505
898
Point Air
149329
265452
216384
5985667
8126
6072
9536
13281181
20632
4511723
55641
7372875
3325311
2727842
2903856
13687
32213
9311
1156914
8960
6028
4400
412960
308927
27671
41693
1090972
795
1159594
319541
434749
182883
1179
70271
1608
803
102624
184C
6
961S
506
122318
266
160907
771
24238
19390
55929
29351
661
113
1229'
423
Water
Discharges
41032
505
1510
25
3558
2162
834
5
2795
555
13561
0
7
10
51
1035
0
876
5
298
1398
809
250
5
0
290
0
0
5

22
0
15
0~
cf
755
250
0
38
Q

209
0
0
6~
0
0
0
0
0
260
37
(
0
Under-
ground
Injection
547
250
76
0
0
0
250
0
0
0
0
0
0
0
0
0
319
48
0
0
0
0
0
0
0
0
0
0
0
0
0
0
o
0~
6"
0
c
0
c
o
o"
c
0
0
0~
0
0
(
0
0
0
0
0
(
0
Land
Disposal

255
0
553
6121
30345
30994
5
763
71335
95457
5
300
133
6600
15574
0
1530
5
283
256
254
0
0
0
10146
0
12785
6829
0
0
0
0
0~
b~
500
3114
0
C
o
250"
0
0
250
0
0
0
(
0
0
0
0

Total
Releases

531090
299620
8968845
41090
63729
71498
18271419
43421
6717615
251704
10582558
4692281
4774195
5320702
37335
82119
19303
1658287
17227
12594
11221
501126
543472
40595
152899
1498389
15777
2157730
575459
1243923
247065
10217
3741
128062
4397
7773
384824
2845
180103
323
25388
7548
167880
542"
198324
26194
34626
33751
667166
51462
5426
161
13195
423
Average
Releases
per Facility

815
768
26693
132
222
264
67923
163
26447
1104
49221
22889
25260
28761
212
469
122
14546
167
135
135
6343
7344
549
2184
24564

37855
10858
25386
5147
107
388T
157
20254
150
20
1587
581
12914
18029"
42l9~

 SIC Code 34
                                          38
        September 1995

-------
Fabricated Metal Products
                                                                 Sector Notebook Project
                                 Exhibit 24 (cont'd)
 Releases for Metal Fabricating & Finishing Facilities (SIC 34) in TRI, by Number
                  of Facilities (Releases reported in pounds/year)
Chemical Name
Bis(2-Ethylhexyl)
Adipate
Dimethyl Phthalate
Phenol
Sec-Butyl Alcohol
Aluminum Oxide
(Fibrous Form)
Di(2-Ethylhexyl)
Phthalate
Dichlorodifluoro-
methane
Silver
Asbestos (Friable)
Barium
Butyl Benzyl Phthalate
Diethyl Phthalate
Molybdenum Trioxide
O-Xylene
Phosphorus (Yellow Or
White)
Toluenediisocyanate
(Mixed Isomers)
2-Methoxyethanol
Ammonium Nitrate
(Solution)
Ammonium Sulfate
(Solution)
Arsenic
Benzene
Diethanolamine
Ethyl Acrylate
Mercury
P-Xylene
Polychlorinated
Biphenyls
Propane Sultone
Selenium
Silver Compounds
2-Dichlorobenzene
2-Nitropropane
4'-
Isopropylidenediphenol
Totals
# Facilities
Reporting
Chemical
4
4
4
4
3
3
3
3
2
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1

Fugitive
Air
8850
2407
12922
6350
250
250
7406
5
10
5
0
255
250
0
10
5
255
0
0
5
3122
0
0
5
0
0
250
5
250
12000
186
0
24,768,891
Point Air
14000
6387
0
19600
250
3000
16443
0
0
0
0
250
0
37928
5
148
24825
0
0
0
836
0
2578
0
22
0
0
0
250
0
182
250
46,819,995
Water
Discharges
0
0
3
0
0
0
0
5
0
0
0
0
0
0
5
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
73,195
Under-
ground
Injection
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1,490
Land
Disposal
0
0
0
0
0
5
0
0
0
0
0
0
2000
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
351,356
Total
Releases
22850
8794
12925
25950
500
3255
23849
10
10
5
0
505
2250
37928
20
153
25080
0
0
5
3958
0
2578
5
22
0
250
5
500
12000
368
250
72,014,927
Average
Releases
per Facility
5713
2199
3231
6488
167
1085
7950
3
5
3
0
253
1125
18964
10
77
12540
0
0
5
3958
0
2578
5
22
0
250
5
500
12000
368
250
....
                     Source: U.S. EPA, Toxics Release Inventory Database, 1993.
September 1995
39
SIC Code 34

-------
Fabricated Metal Products
                    Sector Notebook Project
                                   Exhibit 25
Transfers for Metal Fabricating & Finishing Facilities (SIC 34) in TRI, by Number
                of Facilities (Transfers reported in pounds/year)
Chemical Name
Sulluric Acid
Hydrochloric Acid
Nitric Acid
Xylcne (Mixed
tsomcrs)
Nickel
Chromium
Manganese
Olycol EJhets
Copper
Methyl Ethyl Kctone
Zinc Compounds
N-Butyl Alcohol
Toluene
1-Trichloroethane
Trichloroethylenc
Chromium
Compounds
Phosphoric Acid
Nickel Compounds
Methyl Isobutyl
Kctone
Cyanide Compounds
Copper Compounds
Lead
Ammonia
Ethylbcnzcnc
Hydrogen Fluoride
Zinc (Fume Or
Dust)
Acetone
Manganese
Compounds
Dichloromcthanc
4-Trimethylbcnzene
Tetrachloroethylene
Mcthnnol
Chlorine
MeUiylenebis(Pheny
tisocyanatc)
Naphthalene
Cobalt
Barium Compounds
Freon 1 13
Lead Compounds
Styrene
Cadmium
Formaldehyde
Aluminum (Fume Or
Dust)
Trichlorofluoro-
mcthanc
Cadmium
Compounds
Elhylcnc Glycol
Propylcne 	
Cumcnc
2-Ethoxyethanol
Cyclohcxanc
# Facilities
Reporting
Chemical
861
652
390
336
311
287
271
269
267
254
228
215
205
189
185
176
175
158
114
103
93
83
79
74
74
70
61
58
57
53
49
48
40
35
33
28
25
19
19
17
16
16
13
13
11
11
11
9
8
7
POTW
Discharges
1132535
446440
37256
51
17355
30170
5093
385087
8784
141
31969
13302
93
65
1083
18099
268375
21635
5
19581
13826
1160
31527
5
382
75982
5
302
647
5
65
29686
4470
0
0
319
12
0
797
0
1829
41510
500
0
1288
22685
0
5
5
0
Disposal
2871580
2768870
309134
10852
367278
465237
834964
55411
653024
32971
4797726
9306
31782
34508
34070
721452
300139
463522
1407
17461
341003
78382
1030
2
2581
219289
19917
221084
5
5
6344
0
750
25420
70
10978
56251
0
198398
12000
8006
5
250
7374
65324
86000
0
0
0
750
Recycling
401 1 148
1472808
946756
1661765
8848547
10143210
8774505
824664
53401212
2787367
23980836
100928
603704
1342465
1045702
1222505
5805346
1839379
813193
12188
11781033
2392024
750
170492
0
666508
705690
1243001
289636
23532
555166
35726
250
250
34926
405387
2079
93230
798893
1180
9432
0
157757
0
27000
17100
0
2020
516
0
Treatment
4636541
3169967
623265
332850
464008
422090
8299
142591
60924
268783
2004640
43711
277628
128708
371432
500300
280512
549790
30029
140767
205196
10184
260
14164
16618
120336
173168
1299
73238
10506
129891
34952
6226
7014
14821
753
20823
21794
1590
750
31506
1611
5460
4263
42512
19170
0
441
0
1250
Energy
Recovery
0
0
0
2139660
0
10
0
2295807
667
4002200
3249
306263
1892116
101194
102092
2981
0
6
471629
0
7
281
0
227471
0
61242
134723
0
26737
58127
6692
80494
0
500
39431
0
0
1917
501
250
0
7202
0
0
0
3110
0
5618
2600
255
Total
Transfers
12651804
7935080
1916411
4151607
9727271
11121986
9623861
3746528
54124861
7107644
30847198
497761
2805323
1606940
1554379
2490098
6669606
2879204
1316263
190497
12341065
2482031
33567
412134
19581
1143857
1033503
1465686
390263
92175
698158
180858
11696
33184
89248
440451
79165
116941
1000179
14180
50773
50328
163967
11637
136124
148065
0
8084
3121
2255
Average
Transfers
per Facility
14694
12170
4914
12356
31277
38753
35512
13928
202715
27983
135295
2315
13685
8502
8402
14148
38112
18223
11546
1849
132700
29904
425
5569
265
16341
16943
25270
6847
1739
14248
3768
292
948
2704
15730
3167
6155
52641
834
3173
3146
12613
895
12375
13460
0
898
390
322
SIC Code 34
40
September 1995

-------
fabricated. Metal Products
                                                                  Sector Notebook Project
                                 Exhibit 25 (cont'd)
Transfers for Metal Fabricating & Finishing Facilities (SIC 34)  in TRI, by Number
                  of Facilities (Transfers reported in pounds/year)
Chemical Name
Isopropyl Alcohol
(Manufacturing
Antimony
Compounds
Cobalt Compounds
M-Xylene
Antimony
Bis(2-Ethylhexyl)
Adipate
Dimethyl Phthalate
Phenol
Sec-Butyl Alcohol
Aluminum Oxide
(Fibrous Form)
Di(2-Ethylhexyl)
Phthalate
Dichlorodifluoromet
hane
Silver
Asbestos (Friable)
Barium
Butyl Benzyl
Phthalate
Diethyl Phthalate
Molybdenum
Trioxide
O-Xylene
Phosphorus (Yellow
Or White)
Toluenediisocyanate
^Mixed Isomers)
2-Methoxyethanol
Ammonium Nitrate
^Solution)
Ammonium Sulfate
(Solution)
Arsenic
Benzene
Diethanolamine
Ethyl Acrylate
Mercury
P-Xylene
Polychlorinated
Biphenyls
Propane Sultone
Selenium
Silver Compounds
2-Dichlorobenzene
2-Nitropropane
4'-Isopropylidene-
diphenol
Totals
# Facilities
Reporting
Chemical
6
5
5
5
4
4
4
4
4
3
3
3
3
2
2
2
2
2
2
2
2
2
1
1
1
1
1
1
1
1
1
1
1
1
1
1
1
....
POTW
Discharges
0
10
15
0
0
6400
0
250
0
0
5
0
10
0
5
0
500
0
0
0
0
5
0
128241
5
0
0
0
5
0
0
0
5
250
0
0
0
2,800,087
Disposal
613
104158
18403
0
0
3145
0
1176
0
0
8440
0
15
73822
10
0
0
419
0
0
0
0
0
0
10
0
0
0
10
0
0
0
10
0
0
0
250
16,352393
Recycling
97513
0
41566
0
3187
0
0
0
0
25000
0
0
250
0
0
0
2052
3900
0
12250
0
0
0
0
0
0
440
0
0
0
0
0
0
4000
0
0
0
149,241,964
Treatment
15
1104
5
109
375
0
269
0
840
0
0
0
0
0
0
0
2061
0
61
0
0
0
0
0
0
0
0
0
0
51
2286
0
0
0
0
95
0
15,433,902
Energy
Recovery
5688
0
1
3819
0
0
1802
0
250
0
0
0
0
0
0
0
0
0
0
0
1374
8520
0
0
0
0
0
0
0
0
0
0
0
0
0
103
0
12,002,720
Total
Transfers
103829
105272
59990
3928
3562
9545
2071
1426
1090
25000
8445
0
275
73822
15
0
4613
4319
61
12250
1374
8525
0
128241
15
0
440
0
15
51
2286
0
15
4250
0
198
250
196,188,152
Average
Transfers
per Facility
17305
21054
11998
786
891
2386
518
357
273
8333
2815
0
92
36911
8
0
2307
2160
, 31
6125
687
4263
0
128241
15
0
440
0
15
51
2286
0
15
4250
0
198
250
....
                     Source: U.S. EPA, Toxics Release Inventory Database, 1993.
September 1995
41
SIC Code 34

-------
Fabricated Metal Products
Sector Notebook Project
             Exhibits 26 - 29 illustrate the TRI releases and  transfers for the
             coating, engraving,  and  allied services portion  (SIC 347) of the
             fabricated metal products industry.  For these activities, solvents, as
             well  as acids, constitute the  largest number  of  TRI  releases.
             Solvents are primarily used during painting operations, while acids
             are used during most finishing operations (e.g., anodizing, chemical
             conversion  coating, electroplating).  The solvents usually produce
             air emissions, contaminated wastewater, and  solid-phase wastes,
             while the  acids  generally  result  in contaminated wastewater.
             Because NPDES permits do not allow low PH levels, the wastewater
             is pretreated to reduce the acidity prior to being discharged from the
             facility.
                                   Exhibit 26
            Top 10 TRI Releasing Metal Finishing Facilities (SIC 347)
Rank
1
2
3
4
5
6
7
8
9
10
Total TRI
Releases in
Pounds
708,285
619,436
492,872
430,781
418,912
408,628
406,419
381,788
368,014
344,572
Facility Name
Plastene Supply Co.
Ken-Koat, Inc.
Tennessee Electroplating, Inc.
SR of Tennessee
Ken-Koat of Tennessee, Inc., Plant 1
Anomatic Corp.
Roll Coaler, Inc.
Reynolds Metals Co., Sheffield
Plant
Roll Coater, Inc.
Mottley Foils, Inc.
City
Portageville
Huntington
Ripley
Ripley
Lewisburg
Newark
Greenfield
Sheffield
Kingsbury
Farmville
State
MO
IN
TN
TN
TN
OH
IN
AL
IN
VA
                    Source:  U.S. hi?A, I oxics Release inventory uataoase, ±yyo.

Note: Being included on this list does not mean that the release is associated with non-compliance
      with environmental laws.
 SIC Code 34
                                         42
       September 1995

-------
 Fabricated. Metal Products
                                                                 Sector Notebook Project
             TRI
                    Exhibit 27
Reporting Metal Finishing Facilities (SIC 347) by State
State
AL
AR
AZ
CA
CO
CT
DE
FL
GA
ffl
IA
IL
IN
KS
KY
LA
MA
MD
ME
ME
MN
Number of
Facilities
19
4
9
117
11
36
1
14
14
1
6
121
49
7
13
5
39
7
1
109
36
State
MO
MS
NC
NE
NH
NJ
NY
OH
OK
OR
PA
PR
RI
SC
TN
TX
UT
VA
WA
WI
wv
Number of
Facilities
23
6
11
1
1
27
43
112
9
11
41
4
23
9
17
48
4
7
14
35
4
                     Source: U.S. EPA, Toxics Release Inventory Database, 1993.
                                     Exhibit 28
      Releases for Metal Finishing (SIC 347) in TRI, by Number of Facilities
                        (Releases reported in pounds/year)
Chemical Name
Sulfunc Acid
Hydrochloric Acid
Nitric Acid
Zinc Compounds
Phosphoric Acid
Methyl Ethyl Ketone
Chromium Compounds
Nickel Compounds
Cyanide Compounds
Nickel
Trichloroethylene
JCylene (Mixed Isomers)
1,1,1 -Trichloroethane
Toluene
Glycol Ethers
Copper
Chromium
N-Butyl Alcohol
Copper Compounds
Ammonia
Chlorine
Lead
# Facilities
Reporting
Chemical
577
490
290
158
120
103
101
95
87
87
81
79
73
69
59
54
48
44
43
35
32
31
Fugitive
Air
159575
229596
51229
75329
24772
945484
4572
5821
6759
4685
844061
395089
763993
375222
344040
880
2517
114102
2874
75738
5828
89
Point Air
103935
186461
140639
23316
26993
2251059
10765
4572
4098
3257
847701
1226943
817417
1566048
1463579
3508
2372
188305
1955
11644
1011
1715
Water
Discharges
38232
505
1510
12202
0
555
625
564
224
1433
20
5
5
5
0
1646
131
0
207
0
5
536
Under-
ground
Injection
0
250
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
Land
Disposal
54450
255
0
93054
0
71335
15
0
283
500
0
0
0
300
0
0
255
0
0
0
0
0
Total
Releases
356192
417067
193378
203901
51765
3268433
15977
10957
11364
9875
1691782
1622037
1581415
1941575
1807619
6034
5275
302407
5036
87382
6844
2340
Average
Releases
per Facility
617
851
667
1291
431
31732
158
115
131
114
20886
20532
21663
28139
30638
112
110
6873
117
2497
214
75
September 1995
                         43
SIC Code 34

-------
Fabricated Metal Products
Sector Notebook Project
                                Exhibit 28 (cont'd)
      Releases for Metal Finishing (SIC 347) in TRI, by Number of Facilities
                       (Releases reported in pounds/year)
Chemical Name
Methyl Isobutyl Kctone
Telraehlorocthylcne
Acetone
Ethylbcnzcne 	
Naphthalene
Zinc (Fume Or Dust)
1.2.4-Trimclhylbenzene
Diehloro methane
Formaldehyde
Mcthonol
Cadmium
Barium Compounds
Hydrogen Fluoride
Cadmium Compounds
Manganese 	
Cumcnc
Cobalt
Ficon 113
Lead Compounds 	
Manganese Compounds
Methylencbis
(Phcnylisocyanate)
Aluminum (Fume Of Dust)
Antimony 	
Dimethyl Phthalale
Ethylcne Glycol
Pfppylene 	
Aluminum Oxide (Fibrous
Form)
Isopropyl Alcohol
(Manufacturing) 	
M-Xylene
Sec-Butyl Alcohol 	
Silver
2-Methoxyethanol
Ammonium Nitrate
(Solution) 	
Arsenic
Barium
Bis(2-Ethylhexyl) Adipate
Ethyl Acrylate
Mercury 	
O-Xylene 	
Plicnol
Selenium
Silver Compounds 	
Trichloronuoro me thane
1 ,2-Dichlorobcnzcne
2-Ethoxyethanol
2-N'ilropropanc
4.4-lsopropylidenediphenol

# Facilities
Reporting
Chemical
30
25
21
20
20
20
20
IS
15
15
13
12
10
9
8
7
6
6
5
4
4
3
3
3
3
3
2
2
2
2
2
2
1














—
Fugitive
Air
127088
401718
166232
46499
25677
14713
87617
420391
14409
53243
57
1601
6216
266
21
9178
12
93785
255
15
5
250
0
2407
1160
503
0
250
0
1000
5
255
0
5
0
0
0
5
0
12000
5
250
5
12000
250
186
0
5,931,789
Point Air
269586
211664
250318
68675
52326
405
118935
395882
8992
138202
6
482
3208
11
69
18933
542
0
500
5
150
250
418
5438
18552
516
0
15000
6109
3000
0
24825
0
0
0
0
2578
0
37911
0
0
250
12000
0
7000
182
250
10,560,463
Water
Discharges
0
0
0
0
0
0
0
5
209
0
0
0
0
0
0
0
5
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
58,629
Under-
ground
Injection
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
250
Land
Disposal
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
220,447
Total
Releases
396674
613382
416550
115174
78003
15118
206552
816278
23610
191445
63
2083
9424
277
90
28111
559
93785
755
20
155
500
418
7845
19712
1019
0
15250
6109
4000
5
25080
0
5
0
0
2578
5
37911
12000
5
500
12005
12000
7250
368
250
16,771,578
Releases
per Facility
13222
24535
19836
5759
3900
756
10328
54419
1574
12763
5
174
942
31
11
4016
93
15631
151
5
39
167
139
2615
6571
340
0
7625
3055
2000
3
12540
0
5
0
0

5
37911
12000
5
500
12005
12000
7250
368
250
—
Source: U.S. EPA, Toxics Release Inventory Database, 1993.
 SIC Code 34
                                          44
       September 1995

-------
 Fabricated Metal Products
                                                              Sector Notebook Project
                                    Exhibit 29
      Transfers for Metal Finishing (SIC 347) in TRI, by Number of Facilities
                       (Transfers reported in pounds/year)
Chemical Name

Hydrochloric Acid
Nitric Acid
Zinc Compounds
Phosphoric Acid
Methyl Ethyl Ketone
Chromium Compounds
Nickel Compounds
Cyanide Compounds
Nickel
Trichloroethylene
Xylene (Mixed Isomers)
1,1,1 -Trichloroethane
Toluene
Glycol Ethers
Copper
Chromium
N-Butyl Alcohol
Copper Compounds
Ammonia
Chlorine
Lead
Methyl Isobutyl Ketone
Tetrachloroethylene
Acetone
Ethylbenzene
Naphthalene
Zinc (Fume Or Dust)
1 ,2,4-Trimethy Ibenzene
Dichloromethane
Formaldehyde
Methanol
Cadmium
Barium Compounds
Hydrogen Fluoride
Cadmium Compounds
Manganese
Cumene
Cobalt
Freon 113
Lead Compounds
Manganese Compounds
Methylenebis
[Phenylisocyanate)
Aluminum (Fume Or Dust)
Antimony
Dimethyl Phthalate
3thylene Glycol
Propylene
Aluminum Oxide (Fibrous
rform)
Isopropyl Alcohol
Manufacturing)
M-Xylene
Sec-Butyl Alcohol
Silver
2-Methoxyethanol
#
Facilities
Reporting
Chemical
J / /
490
290
158
120
103
101
95
87
87
81
79
73
69
59
54
48
44
43
35
32
31
30
25
21
20
20
20
20
15
15
15
13
12
10
9
8
7
6
6
5
4
4
3
3
3
3
3
2
2
2
2
2
2
POTW
Discharges
oU4yoo
382255
32756
25225
160428
10
14423
17937
18577
12239
353
10
45
6
206381
3810
4297
13300
8404
19727
4210
61
0
20
5
0
0
4580
0
377
41510
29686
1814
5
0
1287
889
0
30
0
751
5
0
250
0
0
5
0
0
0
0
0
5
5
Disposal
1947304
2691567
274177
4286331
296366
0
594848
375149
16451
255282
4873
2465
1090
3248
4168
215903
253964
1615
109090
260
750
10814
0
0
0
0
0
9250
0
0
5
0
6186
26665
2581
65319
851
0
7590
0
1520
22024
0
0
0
0
0
0
0
0
0
0
10
0
Recycling
3112900
1467208
822830
16726872
5126632
2060497
249365
1171327
12127
777750
214013
373083
359456
323174
209411
4247604
245168
19334
3397732
0
250
428225
467583
198381
482911
95670
1000
181479
12825
92499
0
1513
9432
29
0
27000
113
2020
1431
3900
42677
87789
0
0
1955
0
0
0
25000
87932
0
0
250
0
Treatment
2266082
3058084
562997
1865137
120242
110831
364291
501971
126143
399252
103537
110740
30856
212714
44590
14524
402593
19951
118222
255
6221
7169
8208
10999
134524
2795
7046
75065
8538
22453
1588
34930
31256
7756
16618
250
1751
400
193
0
319
0
0
5460
375
269
250
0
0
0
0
0
0
0
Energy
Recovery
0
0
0
2994
0
1994068
2980
0
0
0
63712
499378
25528
912937
530166
0
0
68165
0
0
0
0
70164
4542
37649
67994
23833
0
37488
15138
7202
56354
0
0
0
0
0
5618
0
0
0
0
0
0
0
1802
994
0
0
2300
0
0
0
8520
Total
Transfers
8131194
7676109
1692760
22906591
5718883
4181588
1244457
2066384
173798
1445523
386488
985676
416975
1452079
994966
4481841
923657
122365
3633448
20242
11431
446269
545955
213942
655089
166459
31879
270624
58851
130467
50305
122483
48688
34455
19199
93856
3604
8038
9244
3900
45267
109818
0
5710
2330
2071
1249
0
25000
90232
0
0
265
8525
Average
Transfers
per
Facility
14092
15666
5837
144978
47657
40598
12321
21751
1998
16615
4771
12477
5712
21045
16864
82997
19243
2781
84499
578
357
14396
18199
8558
31195
8323
1594
13531
2943
8698
3354
8166
3745
2871
1920
10428
451
1148
1541
650
9053
27455
0
1903
111
690
416
0
12500
45116
0
0
133
4263
September 1995
45
SIC Code 34

-------
Fabricated Metal Products
Sector Notebook Project
                              Exhibit 29 (cont'd)
     Transfers for Metal Finishing (SIC 347) in TRI, by Number of Facilities
                      (Transfers reported in pounds/year)
Chemical Name
Ammonium Nitrate
(Solution)
Arsenic
Barium
Bis(2-Elhylhexyl) Adipale
Ethyl Acrylale 	
Mercury 	
O-Xylene 	
Phenol
Selenium 	
Silver Compounds 	
Trichlorofluoromethane
1.2-Diehlorobcnzene 	
2-Ethoxyethanol 	
2-Nilropropane 	
4.4-Isopropylidenediphenol

#
Facilities
Reporting
Chemical
1










—
POTW
Discharges
0
5
5
0
0
5
0
5
250
0
5
0
0
1,810,861
Disposal
0
10
10
250
0
10

-------
UaVticated. Metal Products
                                                             Sector Notebook Project
Acetone
             information contained below is based upon exposure assumptions
             that have been conducted using standard scientific procedures. The
             effects listed  below must  be taken  in  context of these exposure
             assumptions that are more fully explained within the full chemical
             profiles in HSDB.

             The top ten TRI releases  for the Fabricated Metal Products industry
             (SIC 34) as a whole include:  glycol ethers, n-butyl, xylene, methyl
             ethyl  ketone,  trichloroethylene,  toluene-1,  dichloromethane,
             methyl isobutyl ketone, acetone, and tetrachloroethylene.  The top
             ten TRI  releases for  the coating,  engraving,  and allied services
             portion of the fabricated  metal products industry (SIC 347) include:
             methyl ethyl  ketone, toluene,  glycol  ethers, trichloroethylene,
             xylene (mixed  isomers), 1,1,1-trichloroethane,  dichloromethane,
             tetrachloroethylene, hydrochloric acid, and methyl isobutyl ketone.
             Summaries of most of these chemicals follow.
             Toxicity.   Acetone is irritating to the  eyes,  nose, and throat.
             Symptoms of exposure to large quantities of acetone may include
             headache, unsteadiness, confusion, lassitude, drowsiness, vomiting,
             and respiratory depression.

             Reactions  of acetone  (see  environmental fate)  in  the  lower
             atmosphere  contribute to the formation of ground-level ozone.
             Ozone (a major component of urban smog) can affect the respiratory
             system, especially in sensitive individuals such as asthmatics or
             allergy sufferers.

             C arcino genicity.  There is currently no evidence to suggest that this
             chemical is carcinogenic.

             Environmental   Fate.   If released into water,  acetone will be
             degraded by microorganisms or will  evaporate into the atmosphere.
(Directory of Biotechnology Information Resources), EMICBACK (Environmental Mutagen
Information Center Backfile), GENE-TOX (Genetic Toxicology), HSDB (Hazardous Substances
Data Bank), IRIS (Integrated Risk Information System), RTECS (Registry of Toxic Effects of
Chemical Substances), and TRI (Toxic Chemical Release Inventory).  HSDB contains chemical-
specific information on manufacturing and use, chemical and physical properties, safety and
handling, toxicity and biomedical effects, pharmacology, environmental fate and exposure
potential, exposure standards and regulations, monitoring and analysis methods, and additional
references.
September 1995
47
SIC Code 34

-------
Fabricated Metal Products
Sector Notebook Project
            Degradation by  microorganisms will be  the  primary removal
            mechanism.

            Acetone is highly volatile, and  once it reaches the troposphere
            (lower atmosphere), it will react  with other gases,  contributing to
            the formation of ground-level ozone and other air pollutants.  EPA
            is reevaluating acetone's reactivity in the lower  atmosphere to
            determine whether this contribution is significant.

            Physical Properties. Acetone is a volatile and flammable organic
            chemical.

            Note:  Acetone  was removed from the list of TRI chemicals on June
            16,  1995 (60 FR 31643)  and will not be reported for 1994 or
            subsequent years.
Glvcol Ethers
            Due to data limitations, data on diethylene glycol (glycol ether) are
            used to represent all glycol ethers.

            Toxicity.  Diethylene glycol is only a hazard to human health if
            concentrated vapors  are generated through  heating  or  vigorous
            agitation or if appreciable skin contact or ingestion occurs over an
            extended period of time.  Under normal occupational and ambient
            exposures, diethylene  glycol is low in oral toxicity, is not irritating to
            the eyes  or skin, is not readily absorbed through the skin, and has a
            low vapor pressure so that toxic concentrations of the vapor can not
            occur in  the air at room temperatures.

            At high levels of exposure, diethylene glycol causes central nervous
            depression and liver  and kidney damage.  Symptoms  of moderate
            diethylene glycol poisoning include nausea,  vomiting,  headache,
            diarrhea, abdominal pain, and damage  to  the  pulmonary and
            cardiovascular systems.  Sulfanilamide  in diethylene glycol was
            once used therapeutically against bacterial infection; it was
            withdrawn from the market after causing over 100  deaths from
            acute kidney failure.

            Carcinogenicity.  There is currently no evidence to suggest that this
            chemical is carcinogenic.
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             Environmental Fate.  Diethylene glycol is a water-soluble, volatile
             organic chemical. It may enter the environment in liquid form via
             petrochemical  plant effluents  or as  an unburned  gas from
             combustion sources. Diethylene glycol typically does not occur in
             sufficient concentrations to pose a hazard to human health.
Hydrochloric Acid

             Toxicity. Hydrochloric acid  is primarily a concern in its aerosol
             form.   Acid  aerosols have been implicated  in causing and
             exacerbating a variety of respiratory ailments. Dermal exposure and
             ingestion of highly concentrated hydrochloric acid can  result in
             corrosivity.

             Ecologically, accidental releases  of  solution forms of hydrochloric
             acid  may  adversely affect aquatic life by including a  transient
             lowering of the pH (i.e., increasing the acidity) of surface waters.

             Carcinogenicity. There is currently no evidence to suggest that this
             chemical is carcinogenic.

             Environmental Fate.  Releases of hydrochloric acid to surface waters
             and soils will be neutralized to an extent due  to the buffering
             capacities of both systems.  The extent of these reactions will depend
             on the characteristics of the specific  environment.

             Physical Properties.  Concentrated hydrochloric  acid  is highly
             corrosive.

Methylene Chloride (Dichloromethane)

             Toxicity.   Short-term exposure to dichloromethane  (DCM)  is
             associated with central  nervous system  effects, including headache,
             giddiness, stupor, irritability, and numbness and tingling in the
             limbs.  More severe neurological effects are reported from longer-
             term exposure, apparently due to increased carbon monoxide in the
             blood from the break down of DCM.  Contact with DCM causes
             irritation of the eyes, skin, and respiratory tract.

             Occupational exposure  to DCM has also  been linked to increased
             incidence of spontaneous abortions in  women.  Acute damage  to
             the eyes and upper respiratory tract, unconsciousness,  and death
            were  reported in workers exposed to high concentrations  of DCM.
            Phosgene (a degradation product of DCM)  poisoning has been
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            reported to occur in several cases where DCM was used in the
            presence of an open fire.

            Populations at special risk from exposure to DCM include obese
            people  (due to accumulation  of DCM  in fat), and people  with
            impaired cardiovascular systems.

            Carcinogenicity. DCM is a probable human carcinogen via both oral
            and inhalation exposure, based on inadequate human data and
            sufficient evidence in animals.

            Environmental  Fate.  When spilled on land, DCM is rapidly lost
            from the soil surface through volatilization.  The remainder leaches
            through the subsoil into the groundwater.

            Biodegradation is possible in natural waters but will probably be
            very slow compared  with evaporation.  Little is known about
            bioconcentration in aquatic organisms or adsorption to sediments
            but these are not likely to be significant processes. Hydrolysis is not
            an important process under normal environmental conditions.

            DCM released into the atmosphere  degrades via contact with other
            gases with a half-life of several months.  A small fraction of the
            chemical diffuses to the stratosphere where it rapidly degrades
            through exposure to ultraviolet radiation and contact with  chlorine
            ions.  Being a moderately soluble chemical, DCM is expected to
            partially return to earth in rain.
Methvl Ethvl Ketone
            Toxicity.  Breathing moderate amounts of methyl ethyl ketone
            (MEK) for short periods of time can cause adverse effects on the
            nervous system ranging from headaches, dizziness, nausea, and
            numbness in the fingers and toes to unconsciousness. Its vapors are
            irritating to  the skin, eyes, nose,  and throat and can damage the
            eyes. Repeated exposure to moderate to high  amounts may cause
            liver and kidney effects.

            Carcinogenicitv. No agreement exists over the  carcinogenicity of
            MEK.  One source believes MEK is a possible carcinogen in humans
            based on limited animal evidence.  Other sources believe that there
            is insufficient evidence to make any statements about  possible
            carcinogenicity.

            Environmental  Fate. Most of the MEK released to the environment
            will end up in the atmosphere.   MEK  can  contribute to the
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 Toluene
             formation of air  pollutants in the lower atmosphere.  It can be
             degraded by microorganisms living in water and soil.

             Physical Properties. Methyl ethyl ketone is a flammable liquid.
             Toxicity. Inhalation or ingestion of toluene can cause  headaches,
             confusion, weakness, and memory loss. Toluene may also affect the
             way the kidneys and liver function.

             Reactions  of toluene (see environmental fate) in  the atmosphere
             contribute to the formation of ozone in the lower atmosphere.
             Ozone  can affect the respiratory system, especially in sensitive
             individuals such as asthma or allergy sufferers.

             Some studies have shown that unborn animals were harmed when
             high levels of toluene were inhaled by their mothers,  although the
             same effects were not  seen when  the  mothers  were fed large
             quantities  of toluene.  Note that these results may reflect similar
             difficulties in humans.

             Carcinogenicity. There is currently no evidence to suggest that this
             chemical is carcinogenic.

             Environmental  Fate.  The majority of releases of  toluene to land
             and water will evaporate.   Toluene may also be degraded by
             microorganisms. Once volatized, toluene in the  lower atmosphere
             will react with other atmospheric components contributing  to the
             formation of ground-level ozone and other air pollutants.

             Physical Properties. Toluene  is a volatile organic chemical.
1,1,1-Trichloroethane
            Toxicity. Repeated contact of 1,1,1-trichloroethane (TCE) with skin
            may cause serious skin cracking and infection.  Vapors cause a slight
            smarting of the eyes or respiratory system if present  in  high
            concentrations.

            Exposure to high concentrations of TCE causes reversible mild liver
            and  kidney dysfunction, central nervous system depression, gait
            disturbances, stupor, coma, respiratory depression, and even death.
            Exposure to lower concentrations of TCE leads to light-headedness,
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            throat irritation, headache, disequilibrium, impaired coordination,
            drowsiness,.convulsions and mild changes in perception.

            Carcinogenicity. There is currently no evidence to suggest that this
            chemical is carcinogenic.

            Environmental Fate.  Releases of TCE to surface water or land will
            almost entirely volatilize. Releases to air may be transported long
            distances and may partially return to earth in rain.  In the  lower
            atmosphere,  TCE degrades very  slowly by photooxidation and
            slowly diffuses to the upper atmosphere where photodegradation is
            rapid.

            Any TCE that does not evaporate from soils leaches to groundwater.
            Degradation in soils and water is slow.  TCE does not hydrplyze in
            water, nor does it significantly bioconcentrate in aquatic organisms.
Trichloroethvlene
            Toxicity.  Trichloroethylene was once used as an anesthetic, though
            its  use caused several fatalities due to liver failure.   Short term
            inhalation exposure to high levels of trichloroethylene may cause
            rapid coma followed by eventual death from liver, kidney, or heart
            failure.    Short-term exposure  to  lower  concentrations  of
            trichloroethylene causes eye, skin, and respiratory tract irritation.
            Ingestion  causes a  burning  sensation in the mouth, nausea,
            vomiting and abdominal pain.  Delayed effects from short-term
            trichloroethylene poisoning  include liver and  kidney lesions,
            reversible nerve degeneration, and psychic disturbances. Long-term
            exposure  can produce headache, dizziness,  weight  loss,  nerve
            damage,  heart damage, nausea, fatigue,  insomnia,  visual
            impairment, mood perturbation, sexual problems,  dermatitis,  and
            rarely  jaundice.    Degradation  products of trichloroethylene
            (particularly phosgene) may cause rapid death due to respiratory
            collapse.

            Carcinogenicitv. Trichloroethylene is a probable human carcinogen
            via both oral and inhalation exposure,  based on limited  human
            evidence and sufficient animal evidence.

            Environmental Fate.  Trichloroethylene breaks  down slowly in
            water in the presence of sunlight and bioconcentrates moderately in
            aquatic  organisms.   The main removal  of trichloroethylene from
            water is via rapid evaporation.
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             Trichloroethylene does  not photodegrade  in the  atmosphere,
             though it breaks down quickly under  smog  conditions, forming
             other  pollutants such  as  phosgene, dichloroacetyl chloride, and
             formyl chloride. In addition,  trichloroethylene vapors may be
             decomposed  to  toxic levels  of phosgene  in  the  presence of an
             intense heat source such as an open arc welder.

             When spilled on the  land, trichloroethylene  rapidly volatilizes
             from surface  soils.  The  remaining chemical leaches  through the
             soil to groundwater.

Xylene (Mixed Isomers)

             Toxicity. Xylenes are rapidly absorbed into the body after inhalation,
             ingestion, or skin contact.  Short-term exposure of humans to high
             levels  of xylenes can cause irritation of the skin, eyes, nose, and
             throat, difficulty in breathing,  impaired lung function,  impaired
             memory, and possible changes in the liver and kidneys.  Both short-
             and long-term exposure to high concentrations can cause effects
             such  as headaches, dizziness,  confusion, and  lack of muscle
             coordination.  Reactions of xylenes (see environmental fate)  in the
             atmosphere contribute to the formation of ozone in the  lower
             atmosphere.  Ozone can affect the respiratory system, especially in
             sensitive individuals such  as asthma or allergy sufferers.

             Carcinogenicity.  There  is  currently no evidence to suggest that this
             chemical is carcinogenic.

             Environmental Pate.  The majority of releases  to land and  water
             will  quickly evaporate,  although  some  degradation  by
             microorganisms will occur.

            Xylenes  are moderately  mobile in soils  and may leach into
            groundwater, where they may persist for several years.

            Xylenes are volatile organic chemicals.  As such, xylenes in the
            lower atmosphere will  react with other  atmospheric components,
            contributing to the formation of ground-level ozone and  other air
            pollutants.
IV.C. Other Data Sources

            The  Aerometric Information Retrieval  System (AIRS)  contains a
            wide range of information related to stationary  sources of air
            pollution, including the emissions of a number  of air pollutants
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            which may be of concern within a particular industry.  With the
            exception  of volatile organic  compounds  (VOCs), there is little
            overlap  with  the TRI  chemicals reported  above.   Exhibit  30
            summarizes annual releases of  carbon monoxide (CO), nitrogen
            dioxide (NO2), particulate matter of 10 microns or less (PM10), total
            particulates (FT), sulfur  dioxide  (SO2), and volatile organic
            compounds (VOCs).

                                  Exhibit 30
                     Pollutant Releases (Short Tons/Years)
Industry

Metal Mining 	
Nonmetal Mining 	
Lumber and Wood Products
Wood Furniture and
Fixtures
Pulp and Paper 	
Printing 	
Inorganic Chemicals 	
Organic Chemicals 	
Petroleum Refining
Rubber and Misc. Plastic
Products
Stone, Clay, Glass, and
Concrete
Iron and Steel
Nonfcrrous Metals
Fabricated Metals
Electronics
Motor Vehicles, Bodies,
Parts, and Accessories

CO

5,391
4,525
123,756
2,069
624,291
8,463
166,147
146,947
419,311
2,090
58,043
1,518,642
448,758
3,851
367
35,303

NO2
23,402,000
28,583
28,804
42,658
2,981
394,448
4,915
108,575
236,826
380,641
11,914
338,482
138,985
55,658
16,424
1,129
23,725
179
PMio
45,489,000

59,305
14,135
2,165
35,579
399
4,107
26,493
18,787
2,407
74,623
42,368
20,074
1,185
207
2,406
3
PT
7,836,000

167,948
63,761
3,178
113,571
1,031
39,082
44,860
36,877
5,355
171,853
83,017
22,490
3,136
293
12,853
28
SO2
21,888,000

24,129
9,149
1,606
341,002
1,728
182,189
132,459
648,153
29,364
339,216
238,268
373,007 .
4,019
453
25,462
152

23,312,000

1,736
41,423
59,426
96,875
101,537
52,091
201,888
309,058
140,741
30,262
82,292
27,375
102,186
4,854
101,275
7,310
Source U.S. EPA Office of Air and Radiation, AIRS Database, May 1995.
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 IV.D.  Comparison of Toxic Release Inventory Between Selected Industries

             The  following  information  is presented as  a comparison of
             pollutant release and transfer data across industrial categories.  It is
             provided to give a general sense as to the relative scale of releases
             and transfers within each sector profiled under this project. Please
             note that the following table does not contain releases and transfers
             for industrial categories that are not included in this project, and
             thus cannot be used to draw conclusions regarding the total release
             and transfer amounts that are reported to TRI.  Similar information
             is available within the  annual TRI Public Data Release book.

             Exhibit 31 is a graphical representation  of  a summary of the 1993
             TRI data for the Fabricated Metals Products industry and the other
             sectors profiled in separate notebooks.  The bar graph presents the
             total TRI releases and total transfers on the left axis and the triangle
             points  show the average releases per  facility on  the right  axis.
             Industry sectors are presented in the order of increasing total TRI
             releases.  The graph is  based on the data shown in Exhibit 32 and is
             meant to facilitate comparisons between the  relative amounts of
             releases, transfers, and releases per facility both within and between
             these sectors. The reader should note, however, that differences in
             the proportion of facilities captured by TRI exist between industry
             sectors.   This can be a factor  of poor  SIC matching and  relative
             differences in the number of facilities  reporting to TRI from the
             various sectors.  In the case of Fabricated Metal Products industry,
             the  1993 TRI data presented here covers  2,363  facilities.  These
             facilities  listed SIC 34 (Fabricated Metal Products  industry)  as a
             primary SIC code.
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V.    POLLUTION PREVENTION OPPORTUNITIES

            The best way to reduce pollution is to prevent it in the first place.
            Some   companies  have  creatively   implemented  pollution
            prevention techniques that improve efficiency and increase profits
            while at the same time minimizing environmental impacts.  This
            can be  done in many ways such  as reducing material inputs, re-
            engineering  processes  to  reuse  by-products,  improving
            management practices,  and  employing  substitution  of toxic
            chemicals.  Some smaller facilities are able to actually  get  below
            regulatory thresholds just by reducing pollutant  releases through
            aggressive pollution prevention policies.

            In order to encourage these approaches, this section provides both
            general and  company-specific descriptions of  some  pollution
            prevention advances that  have  been  implemented within the
            Fabricated  Metal   Products industry.   While  the list is  not
            exhaustive, it does provide core information that can be used as the
            starting point for facilities interested in  beginning their own
            pollution prevention projects.  When possible, this section provides
            information from real activities that can, or are being implemented
            by this sector ~ including  a discussion of associated costs, time
            frames, and  expected rates of return.   This  section  provides
            summary information from activities that may be,  or  are being
            implemented by this sector.   When  possible, information  is
            provided that gives  the  context in which the  techniques can be
            effectively used.  Please  note  that the activities described in this
            section do not necessarily apply to all facilities that fall within this
            sector.   Facility-specific  conditions must  be carefully considered
            when  pollution  prevention options are evaluated,  and the full
            impacts of  the change must examine how each option affects, air,
            land, and water pollutant releases.


V.A.     Identification of Pollution Prevention Activities in Use and
          Environmental and Economic Benefits of Each Pollution Prevention
          Activity

            Pollution prevention (sometimes referred to as source reduction) is
            the use of materials, processes, or practices that reduce or eliminate
            the creation of pollutants  or wastes  at  the source.   Pollution
            prevention includes practices  that reduce  the use  of  hazardous
            materials, energy, water or other resources,  and practices that protect
            natural resources through conservation or more efficient use.
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             EPA and the Fabricated Metal  Products industry  are working
             together  to promote pollution prevention because it is often the
             most cost-effective way to reduce  pollution and the associated risks
             to human health and the environment.  Pollution prevention is
             often cost effective because it may  reduce raw material losses; reduce
             reliance on  expensive "end-of-pipe" treatment technologies and
             disposal  practices; conserve  energy, water, chemicals, and other
             inputs; and  mitigate the potential liability associated with  waste
             generation and  disposal.   Pollution prevention often  involves
             complex re-engineering however,  and companies must balance the
             desired savings  in materials  and  benefits  to the  environment
             against the cost of changing operating practices.

             All companies in the Fabricated Metal Products industry, regardless
             of their size,  must comply with environmental regulations related
             to metal fabricating and/or metal finishing processes. Therefore, all
             companies benefit from  the knowledge  of pollution prevention
             techniques which, if implemented, may increase a company's ability
             to meet these requirements.  Many large companies have been
             successful in identifying and implementing pollution prevention
             and  other techniques allowing them  to operate in  an  efficient and
             environmentally protective manner.   This capability may be due in
             part because  large companies often have resources to devote to
             tracking and  implementing pollution prevention techniques, and
             maintaining  an awareness and understanding of regulations that
             apply to their facilities.

             Smaller companies may have limited resources to  devote to  these
             activities, which  may   make monitoring  and  understanding
             regulations more difficult and may result in  limited  pollution
             prevention participation.   Increased  awareness  and publication of
             pollution prevention techniques improve the ability of companies
             to comply with regulations.   Pollution prevention  techniques also
             permit  industrial processes to be more efficient and less costly,
             providing all  companies  with an opportunity to maximize the
             efficiency of their operations and reduce their costs while protecting
             the environment.

             Pollution Prevention techniques and processes currently  used by
             the metal fabricating and finishing industry can be grouped into
             seven general categories:

             •     Production planning and sequencing
             •     Process or equipment modification
             •     Raw material substitution or elimination
             •     Loss prevention and housekeeping
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            «     Waste segregation and separation
            •     Closed-loop recycling
            •     Training and supervision.

            Each of these categories is discussed briefly below.  Refer to Section
            V.D. for a list  of  specific pollution  prevention  techniques and
            associated costs, savings, and other information. It should be kept
            in mind that  every pollution prevention  option may not be
            available for each facility.

            Production  planning  and sequencing is used to ensure that only
            necessary operations are performed and  that  no operation is
            needlessly  reversed or obviated by a following operation.   One
            example is  to sort out substandard  parts  prior to painting or
            electroplating.  A second example is to reduce the frequency with
            which equipment requires cleaning by painting all products of the
            same color at the same time.  A third example is to schedule batch
            processing in a manner that allows the wastes or residues  from one
            batch  to be used as an input for the subsequent batch (e.g., to
            schedule paint formulation from lighter shades to darker) so that
            equipment need not be cleaned between batches.

            Process or equipment modification is used to reduce the amount of
            waste  generated. For example, manufacturers can change to a paint
            application  technique that is more  efficient than spray  painting,
            reduce overspray by reducing the atomizing air pressure, reduce
            drag-out by reducing the withdrawal speed of parts from plating
            tanks, or improve a plating line by incorporating drag-out recovery
            tanks or reactive rinsing.

            Raw  material  substitution or  elimination is the replacement of
            existing raw materials with other materials that produce less waste,
            or a non-toxic waste.  Examples include substituting alkali washes
            for solvent degreasers, and replacing oil with lime or borax soap as
            the drawing agent in cold forming.

            Loss   prevention  and   housekeeping  is  the  performance  of
            preventive   maintenance  and   equipment   and  materials
            management so as  to minimize opportunities for leaks,  spills,
            evaporative losses, and other releases of potentially toxic chemicals.
            For example, spray guns can be cleaned in a manner that does not
            damage leather packings and cause  the guns to leak; or drip pans
            can be placed under leaking machinery to  allow recovery  of the
            leaking fluid.
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             Waste segregation and separation involves avoiding the mixture of
             different types of wastes and avoiding the mixture of hazardous
             wastes with non-hazardous wastes.  This makes the recovery of
             hazardous wastes easier by minimizing  the number of different
             hazardous constituents in a given waste stream.  It also prevents the
             contamination of non-hazardous wastes.  Specific examples include
             segregating scrap metal by metal type, and segregating different
             kinds of used oils.

             Closed-loop recycling  is the on-site use or reuse of a waste as an
             ingredient or feedstock in the production process. For example, in-
             plant paper fiber waste can be collected and recycled to make pre-
             consumer recycled paper products.

             Training  and  supervision  provides  employees  with  the
             information and the  incentive to minimize waste generation in
             their daily duties.  This might include  ensuring that  employees
             know and practice proper and  efficient use of tools and supplies,
             and that they  are aware of, understand, and support the company's
             pollution prevention goals.
V.B.  Possible Pollution Prevention Future Trends

            There are numerous pollution prevention trends  in the metal
            fabrication and finishing industry.  These include recycling liquids,
            employing better waste control techniques, using mechanical forms
            of surface preparation, and/or substituting raw materials.  One
            major trend is the increased recycling (e.g., reuse) of most process
            liquids (e.g., rinse water, acids, alkali cleaning compounds, solvents,
            etc.) used during the metal forming  and finishing processes.  For
            instance, instead of discarding  liquids,  companies are containing
            them and  reusing  them to cut down on the volume of process
            liquids that must eventually be disposed  of.  Also, many companies
            are replacing aqueous plating with ion vapor deposition.

            Another common approach to reducing pollution is to reduce rinse
            contamination via drag-out by slowing and  smoothing the  removal
            of parts (rotating them if necessary), maximizing drip time, using
            drainage boards to  direct dripping solutions back to process tanks,
            and/or installing drag-out  recovery tanks to capture dripping
            solutions.   By  slowing   down the  processes and developing
            structures to contain the  dripping solutions, a facility can better
            control the potential wastes emitted.
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            To reduce the use of acids when cleaning parts, the industry is using
            and encouraging  the  use  of mechanical scraping/scrubbing
            techniques to  clean and prepare the metal  surface.  Emphasizing
            mechanical approaches would greatly diminish the need for acids,
            solvents, and alkalis.  In addition to the mechanical technique for
            cleaning surfaces, companies are encouraged to substitute acids and
            solvents with less harmful liquids (e.g., alcohol). Section V.D. lists
            numerous specific pollution prevention techniques that have been
            employed in the industry.
V.C.  Pollution Prevention Case Studies

            Numerous  pollution  prevention case  histories  have  been
            documented for the metal fabricating and finishing industries.
            Many of these  have dealt primarily with electroplating or general
            finishing operations.  The  Eastside Plating case, presented in this
            section, is a classic example of the numerous pollution prevention
            techniques that can be implemented at an electroplating  company.
            For  other  pollution prevention  case studies, see section V.D.
            PoUution Prevention Options, and the list of pollution prevention
            contacts in section V.E.

            Eastside Plating, an Oregon-based company, has made money
            complying  with  new  environmental  regulations.   Under  the
            direction of its Maintenance  and Water Treatment Manager,  the
            electroplating  firm  implemented  operational  changes  that save
            more than $300,000 annually.   Eastside Plating management  made
            the  commitment to implement a hazardous waste  reduction
            program in 1982.  By  changing  rinsing  techniques, substituting
            materials,  and segregating wastes for treatment, the firm  has
            become a more cost-effective operation.

            By setting priorities and upgrading in phases, the firm was able to
            work toward compliance yet  meet increased demand for  services
            during a period of rapid growth. The first operational modification
            addressed  counterflow  and cascade rinsing systems.  The  changes
            decreased  water used for rinsing, a process that accounts for 90
            percent of all water used in electroplating.  In counterflow rinsing,
            water is  used a number of  times, thus  dramatically reducing
            volume.  Cascade rinsing requires only one  tank with a center
            divider which allows  water  to  spill into the other side.   The
            filling/draining process is continuous and very slow to reduce the
            amount of water used.  Both systems cut water bills and wastewater
            treatment costs.
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            Management next searched for waste treatment chemicals  that
            decreased, rather than increased, the production of sludge. Total
            chromium and cyanide wastes were cut in half simply by changing
            reducing agents.  Chromium acid wastes are now oxidized by using
            sodium bisulfite and sulfuric acid instead of ferrous sulfate, while
            cyanide reduction  is now accomplished more efficiently  with
            gaseous, instead of liquid, chlorine.

            Eastside Plating also upgraded its three major waste treatment
            components:  the cyanide oxidation tank, the chromium reduction
            tank, and  the acid/alkaline neutralizing tank.  The goal  was to
            separate tank flow, eliminate contamination of the acid/alkaline
            neutralizing tank, and  increase efficiency.  Automated  metering
            equipment reduced the quantity of costly caustic chemicals  needed
            to treat acid wastes by 50 percent.  To eliminate the risks associated
            with pump failure and the equalize flow rate, cyanide and chromic
            acid oxidation and reduction tanks were redesigned as gravity flow
            systems. Additionally, plumbing was segregated to prevent cross-
            contamination.   These  simple  solutions  saved Eastside  Plating
            hundreds of thousands of dollars.

            Next, management consulted  with suppliers  when they modified
            the company's mixing sump (sometimes called a reaction tank)  and
            a flocculent mix tank (sometimes called a neutralizing tank).   The
            modification to each prohibits  'indigestion1 in the mixing sump
            interfering with the neutralization  process.  The suppliers  helped
            resolve the  problems   of  inadequate  mixing by  baffling  the
            neutralization tank.

            Since employees can make or break the best anti-pollution plan,
            Eastside Plating offers an extensive employee education program.
            The company says "it's a matter of changing how we do business."
            In addition, Eastside Plating's Safety Committee helps all employees
            work together more safely.  Additionally, the company reported  that
            working with regulators helped the company make the move
            toward compliance:  "The City of Portland and  the Department of
            Environmental Quality were more interested in helping us solve
            our problems than in blaming us."

Industry Pollution Prevention Activities

            Several pollution prevention initiatives focus on the fabricated
            metal products industry.  As identified below, some efforts include
            Georgia's Pollution Prevention Assistance Division (P^AD) strategy,
            the Industrial Technology Corporation collaborative  effort, and the
            Merit Partnership.
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Georgia Department of Natural Resources

            A core strategy of the Pollution Prevention Assistance Division
            (P2AD) of the Georgia Department of Natural Resources (DNR) is to
            focus technical assistance efforts on Georgia manufacturers that
            release chemicals posing the greatest risk to the public and the
            environment.  After reviewing those industries which  provide
            significant opportunities for pollution prevention, various
            strategies will be developed, including on-site technical assistance,
            financial assistance, fact sheets, workshops, and other outreach
            activities that will help manufacturers reduce their generation of
            toxic chemicals. The first phase is an on-going targeting effort,
            which evaluates waste generation characteristics of Georgia
            manufacturers producing toxic and hazardous wastes. The
            fabricated metal products industry was selected as a high priority
            manufacturing sector, along with the paper and paper products
            industry, chemical and allied products industry, transportation
            equipment industry, rubber and plastic products, and printing and
            publishing.
1TAC
             The Industrial Technology Assistance Corporation (ITAC), in
             collaboration with the New York Branch of the AESF, the New
             York Masters Association of Metal Finishers, Utility Metal Research
             Corporation, and ten electroplating companies applied for and
             received funding to deliver a program coordinated and written by
             the Wastewater Technology Center of Canada. This is an industry-
             specific hands on 24 hour training session that integrates the
             assessment and incorporation of pollution  prevention techniques
             into all types of electroplating and metal finishing operations. The
             training also includes an economic evaluation of the benefits of
             resource recovery on a multi-media basis.
Merit  Partnership
             The Merit Partnership brings industry and government
             representatives together to identify pollution prevention needs and
             accelerate pollution prevention technology diffusion.  Merit
             partners and participants include EPA Region 9, The Metal
             Finishing Association of Southern California (MFASC), the
             National Institute of Standards and Testing/California
             Manufacturing Technology Center, EPA's Office of Research and
             Development/Risk Reduction Engineering Lab, large  companies
             processing pollution prevention technologies applicable to the
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              metal finishing industry, local regulatory agencies, and participating
              companies. The Merit Partnership is working closely with its
              members to develop metal finishing projects that are transferable to
              small businesses. There is an emphasis on having large companies
              that are  involved with metal finishing share their proven metal
              finishing methods with smaller companies.   The Merit  Partnership
              and MFASC have already begun to identify programmatic areas for
              metal plating pollution prevention opportunities,  from which
              potential projects will be chosen.
V.D.  Pollution Prevention Options
V.D.I.

Technique
The  following  sections  list  numerous  pollution  prevention
techniques that may be useful to companies specializing in metal
fabrication and finishing operations.  These are options available to
facilities, but are  not to be  construed  as  requirements.   The
information  is organized by metal  shaping,  surface preparation,
plating, and  other finishing operations.

Metal Shaping Operations

Production Planning and  Sequencing
       Option 1 - Improve scheduling of processes that require use of varying oil types in order to
       reduce the number of cleanouts.

Technique - Process  or  Equipment Modification

       Option 1 - Standardize the oil types used for machining, turning, lathing, etc.  This reduces
       the number of equipment cleanouts, and the amount of leftovers and mixed wastes.

       Option 2 - Use specific pipes and lines for each set of metals or processes that require a
       specific oil in order to reduce the amount of cleanouts.

       Option 3 - Save on coolant costs by extending machine coolant life through the use of a
       centrifuge  and the addition of biocides. Costs and Savings: Waste Savings/Reductions: 25
       percent reduction in plant-wide waste coolant generation. Product/Waste Throughput
       Information: based on handling 20,600 gallons of coolant per year.

       Option 4 - Install a second high speed centrifuge on a system already operating with a
       single centrifuge to improve recovery efficiency even more. Costs and Savings: Capital
       Investment: $126,000. Payback Period: 3.1 years. Product/Waste Throughput Information:
       based on handling 20,600 gallons of coolant per year.

       Option 5 - Install a chip wringer to recover excess coolant on aluminum chips. Costs and
       Savings: Capital Investment: $11,000 to $23,000 (chip wringer and centrifuge
       system) .Payback Period: 0.9 years. Product/Waste Throughput Information: based on
       handling 20,600 gallons of coolant per year.
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       Option 6 - Install a coolant recovery system and collection vehicle for machines not on a
       central coolant sump.  Costs and Savings: Capital Investment: $104,000.  Payback Period:
       1.9 years.  Product/Waste Throughput Information: based on handling 20,600 gallons of
       coolant per year.

       Option 7 - Use a coolant analyzer to allow better control of coolant quality. Costs and
       Savings:  Capital Investment: $5,000. Payback Period: 0.7 years. Product/Waste
       Throughput Information: based on handling 20,600 gallons of coolant per year.

       Option 8 - Use an ultrafiltration system to remove soluble oils from wastewater streams.
       Costs and Savings:  Annual Savings: $200,000 (in disposal costs).  Product/Waste
       Throughput Information: based on a wastewater flow rate of 860 to 1,800 gallons per day.

       Option 9 - Use disk or belt skimmers to remove oil from machine coolants and prolong
       coolant life.  Also, design sumps for ease of cleaning.  Costs and Savings:  Waste
       Savings/Reduction: coolant is now disposed once per year rather than 3-6 times per year.

Technique - Raw  Material  Substitution

       Option 1 - In cold forming or other processes where oil is used only as a lubricant, substitute
       a hot lime bath or borax soap for oil.

       Option 2  - Use a stamping lubricant that can remain on the piece until the annealing
       process, where it is burned off. This eliminates the need for hazardous degreasing solvents
       and alkali cleaners.  Costs and Savings: Annual Savings: $12,000 (results from reduced
       disposal, raw material, and labor costs). Waste Throughput Information: The amount of
       waste solvents and cleaners was reduced from 30,000 pounds in 1982 to 13,000 pounds in 1986.
       Employee working conditions were also improved by removing vapors associated with the
       old cleaners.

Technique - Waste  Segregation and Separation

       Option 1 - If filtration or reclamation of oil is required before reuse, segregate the used oils
       in order to prevent mixing wastes.

       Option 2 - Segregation of metal dust or scrap by type often increases the value of metal for
       resale (e.g., sell metallic dust to a zinc smelter instead of disposing of it in a landfill).
       Costs and Savings: Capital Investment: $0. Annual Savings: $130,000. Payback Period:
       immediate. Waste Savings/Reduction: 2,700 tons per year.  (Savings will vary with metal
       type and  market conditions.)

       Option 3 - Improve housekeeping techniques and segregate waste streams (e.g., use care
       when cleaning cutting equipment to prevent the mixture of cutting oil and cleaning solvent).
       Costs and Savings: Capital Investment: $0.  Annual Savings: $3,000 in disposal costs.
       Waste Savings/Reduction:  66 percent (30 tons reduced to 10 tons).

Technique -  Recycling

        Option 1 - Where possible, recycle  oil from cutting/machining operations. Often oils need
       no treatment before recycling. Costs and Savings: Capital Investment: $1,900,000. Annual
        Savings:  $156,000.  Waste Throughput Information: 2 million gallons per year. Facility
        reclaims oil and metal from process water.
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        Option 2 - Oil scrap mixtures can be centrifuged to recover the bulk of the oil for reuse.

        Option 3 - Follow-up magnetic and paper filtration of cutting fluids with ultrafiltration.
        By so doing, a much larger percentage of cutting fluids can be reused.  Costs and Savings:
        Capital Investment: $42,000 (1976). Annual Savings: $33,800 (1980).

        Option 4 - Perform on-site purification of hydraulic oils using commercial "off-the-shelf"
        cartridge filter systems. Costs and Savings:  Capital Investment: $28,000. Annual Savings:
        $17,800/year based on operating costs, avoided new oil purchase, and lost resale revenues.
        Payback Period: less than 2 years.  Product/Waste Throughput Information: example
        facility handles 12,300 gallons/year of waste hydraulic oil.

        Option 5 - Use a continues flow treatment system to regenerate and reuse aluminum chemical
        milling solutions. Costs and Savings: Capital Investment: $465,000. Annual Savings:
        $342,000. Payback Period:  less than 2 years.  Waste Savings/Reduction: 90 percent

        Option 6 - Use a settling tank (to remove solids) and a coalescing unit (to remove tramp oils)
        to recover metal-working fluids.  Costs and Savings: Annual Savings: $26,800 (resulting
        from reduced material, labor, and disposal costs).

V.D.2.       Surface Preparation  Operations

SOLVENT CLEANING

Technique  - Training  and  Supervision

        Option 1 - Improve solvent management by requiring employees to obtain solvent through
        their shop foreman. Also, reuse "waste" solvents from cleaner up-stream operations in
        down-stream, machines shop-type processes.  Costs and Savings:  Capital Investment: $0.
        Annual Savings: $7,200. Waste Savings/Reduction 49 percent (310 tons reduced to 152 tons).
        Product/Waste Throughput Information:  original waste stream history: reactive anions
        (6,100 gallons/year), waste oils (1,250 gallons/year), halogenated solvents (500
        gallons/year).

Technique - Production Planning and  Sequencing

        Option 1 - Pre-cleaning will extent the life of the aqueous or vapor degreasing solvent
        (wipe, squeeze, or blow part with air, shot, etc.). Costs and Savings:  Annual Savings:
        $40,000.  Payback Period:  2 years. Waste Savings/Reduction: 48,000 gallons of aqueous
        waste. Aluminum shot was used  to preclean parts.

        Option 2 - Use countercurrent solvent cleaning (i.e., rinse initially in previously used solvent
        and progress to new, clean solvent).

        Options  3 - Cold clean with a recycled mineral spirits stream to remove the bulk of oil
        before final vapor degreasing.

        Option 4 - Only degrease parts that must be cleaned. Do not routinely degrease all parts.
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Technique - Process  or Equipment  Modification

       Option 1 - The loss of solvent to the atmosphere from vapor degreasing equipment can be
       reduced by:
       •   increasing the freeboard height above the vapor level to 100 percent of tank width;
       •   covering the degreasing unit (automatic covers are available);
       •   installing refrigerator coils (or  additional coils) above the vapor zone;
       •   rotating parts before removal from the vapor degreaser to allow all condensed solvent
           to return to degreasing unit;
       •   controlling the speed at which parts are removed (10 feet or less per minute is
           desirable) so as not to disturb the vapor line;
       •   installing thermostatic heating  controls on solvent tanks; and
       •   adding in-line filters  to prevent particulate buildup in the  degreaser.

       Option 2 - Reduce grease accumulation by adding automatic oilers to avoid excess oil
       applications.

       Option 3 - Use plastic blast media  for paint stripping rather than conventional solvent
       stripping techniques. Costs and Savings: Waste Savings/Reduction: volume of waste
       sludge is reduced by as much as 99 percent over chemical solvents; wastewater fees are
       eliminated.

Technique - Raw Material  Substitution

       Option 1 - Use less hazardous degreasing agents such as petroleum solvents or alkali
       washes.  For example, replace halogenated solvents (e.g., trichloroethylene) with liquid
       alkali cleaning compounds.  (Note that compatibility of aqueous cleaners with wastewater
       treatment systems should be ensured.) Costs  and Savings: Capital Investment: $0. Annual
       Savings: $12,000. Payback Period: immediate. Waste Savings/Reduction: 30 percent of
       1,1,1-trichloroethane replaced with an aqueous cleaner.

       Option 2 - Substitute chromic acid cleaner with non-fuming cleaners such as sulfuric acid
       and hydrogen peroxide. Costs and Sayings: Annual Savings: $10,000 in treatment
       equipment costs and $2.50/lb. of chromium in treatment chemical costs. Product/Waste
       Throughput Information: rinse water flowrate of 2 gallons per minute.

       Option 3 - Substitute less polluting cleaners such as trisodium phosphate or ammonia for
       cyanide cleaners.  Costs and Savings: Annual Savings: $12,000 in equipment costs and
       $3.00/lb.  of cyanide in treatment chemical costs. Product/Waste Throughput Information:
       rinse water flowrate of 2  gallons per minute.

Technique  -  Recycling

        Option 1 - Recycle spent degreasing solvents on site using batch stills.  Costs and Savings:
        Capital Investment: $2,600-$4,100  and $4,200-$17,000.  Product Throughput Information:
        35-60 gallons per hour and 0.6-20 gallons per hour, respectively. Two cost and throughput
        estimates for distillation  units from two vendors.

        Option 2 - Use simple batch distillation to extend the life of 1,1,1-trichloroethane. Costs
        and Savings: Capital Investment:  $3,500(1978).  Annual Savings: $50,400.  Product/Waste
        Throughput Information: facility  handles 40,450 gaUons 1,1,1-trichloroethane per year.
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        Option 3 - When on-site recycling is not possible, agreements can be made with supply
        companies to remove old solvents. Costs and Savings: Capital Investment: $3,250 for a
        temporary storage building. Annual Savings: $8,260. Payback Period: less than 6 months.
        Waste Savings/Reduction: 38,000 pounds per year of solvent sent off site for recycling.

        Option 4 - Arrange a cooperative agreement with other small companies to centrally
        recycle solvent.
 CHEMICAL TREATMENT

 Technique -  Process or  Equipment Modification

        Option 1- Increase the number of rinses after each process bath and keep the rinsing counter-
        current in order to reduce drag-out losses.

        Option 2 - Recover unmixed acids in the wastewater by evaporation.

        Option 3 - Reduce rinse contamination via drag-out by:
        •  slowing and smoothing removal of parts, rotating them if necessary;
        •  using surfactants and other wetting agents;
        •  maximizing drip time;
        •  using drainage boards to direct dripping solutions back to process tanks;
        •  installing drag-out recovery tanks to capture dripping solutions;
        •  using a fog spray rinsing technique above process tanks;
        •  using techniques such as air knives or squeegees to wipe bath solutions off of the part;
           and
        •  changing bath temperature or concentrations to reduce the solution surface tension.

        Option 4 - Instead of pickling brass parts in nitric acid, place them in a vibrating apparatus
        with abrasive glass marbles or steel balls. A slightly acidic additive is used with the
        glass marbles, and a slightly basic additive is used with the steel balls. Costs and Savings:
        Capital Investment:  $62,300  (1979); 50 percent less than conventional nitric acid pickling.

        Option 5 - Use mechanical scraping instead of acid solution to remove oxides of titanium.
        Costs and Savings:  Annual Savings:  $0; cost of mechanical stripping equals cost of chemical
        disposal.  Waste Savings/Reduction:  100 percent.  Waste Throughput Information:
        previously disposed 15 tons/year of acid with metals.

        Option 6 - For cleaning nickel and titanium alloy, replace alkaline etching bath with a
        mechanical abrasive system that uses a silk and carbide pad and pressure to clean or
        "brighten" the metal.  Costs and Savings: Capital Investment: $3,250.  Annual Savings:
        $7,500. Waste Savings/Reduction: 100 percent. Waste Throughput Information:  previous
        etching bath  waste total was  12,000 gallons/year.

        Option 7 - Clean copper sheeting mechanically with a rotating brush machine that scrubs
        with pumice, instead of cleaning with ammonium persulfate, phosphoric acid, or sulfuric
        acid; may generate non-hazardous waste sludge. Costs and Savings: Capital Investment:
        $59,000.  Annual Savings:  more than  $15,000.  Payback Period: 3 years. Waste
        Savings/Reduction:  40,000 pounds of copper etching waste reduced to zero.
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       Option 8- Reduce molybdenum concentration in wastewaters by using a reverse
       osmosis/precipitation system.  Costs and Savings: Capital Investment:  $320,000. Waste
       Throughput Information: permeate capacity of 18,000 gallons per day.  Savings Relative to
       an Evaporative System: installed capital cost savings:  $150,000; annual operating cost
       savings:  $90,000.

       Option 9 - When refining precious metals, reduce the acid/metals waste stream by
       maximizing reaction time in the gold and silver extraction process. Costs and Savings:
       Capital Investment: $0. Annual Savings:  $9,000. Waste Savings/Reduction: 70 percent
       (waste total reduced from 50 tons to 15 tons).

Technique - Raw Material  Substitution

       Option 1 - Change copper bright-dipping process from a cyanide dip and chromic acid dip to
       a sulfuric acid/hydrogen peroxide dip. The new bath is less toxic and copper can be
       recovered.

       Option 2 - Use alcohol instead of sulfuric acid to clean copper wire. One ton of wire requires
       4 liters of alcohol solution, versus 2 kilograms of sulfuric acid. Costs and Savings: Capital
       Investment: $0.

       Option 3 - Replace caustic wire cleaner with a biodegradable detergent.

       Option 4 - Replace chromated desmutting solutions with nonchromated solutions for
       alkaline etch cleaning of wrought aluminum. Costs and Savings: Annual Savings: $44,541.
       Waste Savings/Reduction: sludge disposal costs reduced by 50 percent.

       Option 5 - Replace barium and cyanide salt heat treating with a carbonate/chloride carbon
       mixture, or with furnace heat treating.

       Option 6 - Replace thermal treatment of metals with condensation of saturated  chlorite
       vapors on the surface to be heated. Costs and Savings: Waste Savings/Reduction: this
       process is fast, nonoxidizing, and uniform; pickling is no longer necessary.

Technique  - Recycling

        Option 1 - Sell waste pickling acids as feedstock for fertilizer manufacture or
       neutralization/precipitation.

        Option 2 - Recover metals from solutions for resale. Costs and Savings:  Annual Savings:
        $22,000.  Payback Period: 14 months.  Company sells copper recovered from a bright-dip
        bath regeneration process employing ion exchange and electrolytic recovery.

        Option 3 - Send used copper pickling baths to a continuous electrolysis process for
        regeneration and copper recovery. Costs and Savings: Capital Investment:  $28,500 (1977).
        Product Throughput Information: pickling 12,000 tons of copper; copper recovery is at the
        rate of 200 gallons/ton of processed copper.

        Option 4 - Recover copper from brass bright dipping solutions using a commercially
        available ion exchange system. Costs and Savings:  Annual Savings: $17,047; based on
        labor savings, coppers sulfate elimination, sludge reduction, copper metal savings, and
        bright dip chemicals savings.  Product Throughput Information: example facility processes
        approximately 225,000 pounds of brass per month.
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        Option 5 - Treat industrial wastewater high in soluble iron and heavy metals by chemical
        precipitation.  Costs and Savings:  Annual Savings: $28,000; based on reduced water and
        sewer rates. Waste Throughput Information:  wastewater flow from facility's "patening"
        line is 100 gallons per minute.

        Option 6 - Oil quench baths may be recycled on site by filtering out the metals.

        Option 7 - Alkaline wash life can be extended by skimming the layer of oil (the skimmed
        oil may be reclaimed).


V.D.3.        Plating Operations

Technique -  Training and. Supervision

        Option 1 - Educate plating shop personnel in the conservation of water during processing
        and in material segregation.

Technique - Production  Planning and Sequencing

        Option 1 - Preinspect parts to prevent processing of obvious rejects.

Technique -  Process  or Equipment Modification

        Option 1 - Modify rinsing methods to control drag-out by:
        •   Increasing bath temperature
        •   Decreasing withdrawal rate of parts from plating bath
        •   Increasing drip time over solution tanks; racking parts to avoid cupping solution within
           part cavities
        •   Shaking, vibrating, or passing the parts through an air knife, angling drain boards
           between tanks
        •   Using wetting agents to decrease surface tension in tank.
        Contact: Braun Intertec Environmental, Inc., and MN Office of Waste Management
        (612) 649-5750.

        Option 2 - Utilize water conservation methods including:
           Flow restrictors on flowing rinses
           Counter current rinsing systems
           Fog or spray rinsing
           Reactive rinsing
           Purified or softened water
           Dead rinses
           Conductivity controllers
           Agitation to assure adequate rinsing and homogeneity in rinse tank
           Flow control valves.
        Contact:  Braun Intertec Environmental, Inc., and MN Office of Waste Management
        (612) 649-5750.

        Option 3 - Implement counter flow rinsing and cascade rinsing systems to conserve
        consumption of water. Costs and Savings:  Costs: $75,000 to upgrade existing equipment and
        purchasing new and used equipment.  Waste Savings/Reduction: reduce water use and
        wastewater treatment costs. Contact: Eastside Plating and OR Department of
        Environmental Quality (800)452-4011.
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       Option 4 - Use drip bars to reduce drag-out. Costs and Savings:  Capital Investment: $100
       per tank.  Savings: $600. Contact: NC Department of Natural Resources & Community
       Development, Gary Hunt (919) 733-7015.

       Option 5 - Use drain boards between tanks to reduce generations of drag-out. Costs and
       Savings:  Capital Investment:  $25 per tank. Savings:  $450. Contact: NC Department of
       Natural Resources & Community Development, Gary Hunt (919) 733-7015.

       Option 6 - Install racking to reduce generations of drag-out.  Costs and Savings: Capital
       Investment: zero dollars. Operating Costs: minimal. Savings:  $600.  Contact: NC
       Department of Natural Resources & Community Development, Gary Hunt (919) 733-7015.

       Option 7 - Employ drag out recovery tanks to reduce generations of drag-out. Costs and
       Savings:  Capital Investment: $500 per tank.  Savings: $4,700. Contact: NC Department of
       Natural Resources & Community Development, Gary Hunt (919) 733-7015.

       Option 8 - Install counter-current rinsing operation to reduce water consumption. Costs and
       Savings:  Capital Investment:  $1,800-2,300. Savings:  $1,350 per year. Waste
       Savings/Reductions: reduce water use by 90-99 percent. Contact: NC Department of
       Natural Resources & Community Development, Gary Hunt (919) 733-7015.

       Option 9  - Redesign rinse tank to reduce water conservation. Costs and Savings: Capital
       Investment: $100. Savings:  $750 per year.  Contact: NC Department of Natural Resources
       & Community Development, Gary Hunt (919) 733-7015.

       Option 10 - Increase parts drainage time to reduce drag-out.  Contact:  City of Los Angeles
       Hazardous and Toxic Material Project, Board of Public Works (213) 237-1209.

       Option 11 - Regenerate plating bath by activated carbon filtration to remove built up
       organic contaminants. Costs and Savings:  Capital Investment: $9,192. Costs: $7,973.
       Savings:  $122,420. Waste Savings/Reduction: 10,800 gallons. Reduce volume of plating
       baths disposed and requirements for virgin chemicals. Contact: EPA Hazardous Waste
       Engineering Research Laboratory, Cincinnati, OH, Harry Freeman.

       Option 12 - Install pH controller to reduce the alkaline and acid concentrations in tanks.
       Contact:  Securus, Inc., and DBA Hubbard Enterprises.

        Option 13 - Install atmospheric evaporator to reduce metal concentrations.  Contact:
       Securus, Inc., and DBA Hubbard Enterprises.

        Option 14 - Install process (e.g., CALFRAN) to reduce pressure to vaporize water at cooler
        temperatures and recycle water by condensing the vapors in another container, thus
        concentrating and precipitating solutes out. Costs and Savings: Waste Savings/Reduction:
        reduce volume and quantity of aqueous waste solutions by recovering pure water. Contact:
        CALFRAN International, Inc., (413) 525-4957.

        Option 15 - Use reactive rinsing and multiple drag-out baths. Costs and Savings: Savings:
        Reduce cost of treating spent process baths and rinse waters. Waste Savings/Reduction:
        increase lifetime of process baths and reduce the quantity or rinse water requiring
        treatment.  Contact:  SAIC, Edward R. Saltzberg.
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        Option 16 - Improve control of water level in rinse tanks, improve sludge separation, and
        enhance recycling of supernatant to the process by aerating the sludge. Costs and Savings:
        Savings: $2,000.  Waste Savings/Reduction:  reduce sludge generation by 32 percent.
        Contact:  NJ Hazardous Waste Facilities Siting Commission, Hazardous Waste Source
        Reduction and Recycling Task Force.

        Option 17 - Install system (e.g., Low Solids Fluxer) that applies flux to printed wiring
        boards, leaving little residue and eliminates the need for cleaning CFCs.  Costs and
        Savings: Waste Savings/Reduction: reduce CFC emissions over 50 percent. Contact: AT&T
        Bell Laboratories, Princeton, NJ.

Technique -  Raw  Material Substitution

        Option 1 - Substitute cyanide plating solutions with alkaline zinc, acid zinc, acid sulfate
        copper, pyrophosphate copper, alkaline copper, copper fluoborate, electroless nickel,
        ammonium silver, halide silver, methanesulfonate-potassium iodide silver, amino or thio
        complex silver, no free cyanide silver, cadmium chloride, cadmium sulfate, cadmium
        fluoborate, cadmium perchlorate, gold sulfite, and cobalt harden gold. Contact: Braun
        Intertec Environmental Inc., and MN Office of Waste Management (612) 649-5750.

        Option 2 - Substitute sodium bisulfite and sulfuric acid for ferrous sulfate in order to oxidize
        chromic acid wastes, and substitute gaseous chlorine for liquid chlorine in order to reduce
        cyanide reduction. Costs and Savings: Savings: $300,000 per year. Waste
        Savings/Reduction: reduces feedstock by 50 percent. Contact: Eastside Plating and OR
        Department of Environmental Quality (800) 452-4011.

        Option 3 - Replace hexavalent chromium with trivalent chromium plating systems.
        Contact: City of Los Angeles Hazardous and Toxic Material Project. Board of Public Works
        (213) 237-1209.

        Option 4 - Replace cyanide with non-cyanide baths.  Contact: City of Los Angeles
        Hazardous and Toxic Material Project, Board of Public Works (213) 237-1209.

        Option 5 - Replace conventional chelating agents such as tartarates, phosphates, EDTA,
        and ammonia with sodium sulfides and iron sulf ates in removing metal from rinse water
        which reduces the amount of waste generated from precipitation of metals from aqueous
        wastestreams. Costs and Savings:  Costs:  $178,830 per year. Savings: $382,995 per year.
        Waste Savings/Reduction: 496 tons of sludge per year.  Contact: Tyndall Air Force Base,
        PL, (904) 283-2942, Charles Carpenter, Dan Sucia, Penny Wilcoff;  and John Beller at EG&G
        (108) 526-1149.

        Option 6 - Replace methylene chloride, 1,1,1-trichloroethane, and perchloroethylene
        (solvent-based photochemical coatings) with aqueous base coating of 1 percent sodium
        carbonate. Costs and Savings:  Waste Savings/Reduction: reduce solvent use by 60 tons per
        year. Contact: American Etching and Manufacturing, Pacoima, CA.

        Option 7 - Replace methanol with nonflammable alkaline cleaners.  Costs and  Savings:
        Waste Savings/Reduction: eliminate 32 tons per year of flammable methyl alcohol.
        Contact: American Etching and Manufacturing, Pacoima, CA.

        Option 8 - Substitute a non-cyanide for a sodium cyanide solution used in copper plating
        baths. Costs and Savings: Waste Savings/Reduction: reduce 7,630 pounds per year.
        Contact: Highland Plating Company, Los Angeles, CA.
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Technique - Waste Segregation  and  Separation

       Option 1 - Wastewaters containing recoverable metals should be segregated from other
       wastewater streams.

Technique - Recycling

       Option 1 - Install ion exchange system to reduce generation of drag-out. Costs and Savings:
       Capital Investment: $78,000. Operating Costs: $3,200 per year. Contact: NC Department
       of Natural Resources & Community Development; Gary Hunt (919) 733-7015.

       Option 2 - Employ reverse osmosis system to reduce generation of drag-out. Costs and
       Savings:  Savings: $40,000 per year. Capital Investment: $62,000. Contact: NC
       Department of Natural Resources & Community Development;  Gary Hunt (919) 733-7015.

       Option 3 - Use electrolytic metal recovery to reduce generation of drag-out. Costs and
       Savings:   Capital Investment: $1,000.  Contact: NC Department of Natural Resources &
       Community Development; Gary Hunt (919) 733-7015.

       Option 4 - Utilize electrodialysis to reduce generation of drag-out. Costs and Savings:
       Capital Investment: $50,000. Contact:  NC Department of Natural Resources & Community
       Development; Pollution Prevention Pays Program Gary Hunt (919) 733-7015.

       Option 5 - Implement evaporative recovery to reduce generation of drag-out. Costs and
       Savings:  Capital Investment: $2,500. Contact: NC Department of Natural Resources &
       Community Development; Gary Hunt (919) 733-7015.

       Option 6- Reuse rinse water. Costs and Savings: Savings:  $1,500 per year. Capital
       Investment: $340 per tank. No direct costs. Contact: NC Department of Natural Resources
       & Community Development; Gary Hunt (919) 733-7015.

       Option 7- Reuse drag-out waste back into process tank. Contact: NC Department of Natural
       Resources & Community Development; Gary Hunt (919)  733-7015.

       Option 8- Recover process chemicals with fog rinsing parts over plating bath.  Contact:
       City of Los Angeles Hazardous and Toxic Material Project, Board of Public Works (213) 237-
       1209.

       Option 9- Evaporate and concentrate rinse baths for recycling. Contact: City of Los Angeles
       Hazardous and Toxic Material Project, Board of Public Works (213) 237-1209.

       Option 10 - Use ion exchange and electrowinning, reverse osmosis, and thermal bonding
       when possible. Contact: City of Los Angeles Hazardous and Toxic Material Project, Board
       of Public Works (213) 237-1209.

       Option 11 - Use sludge slagging techniques to extract and recycle metals.  Costs and Savings:
       Capital Investment: $80,000 for 80 tons/year and $400,000 for 1,000 tons/year. Operating
       Costs: $18,000 per year for an 80 ton facility. Waste Savings/Reduction:  reduces volume of
       waste by 94 percent. Contact: City of Los Angeles Hazardous and Toxic Material Project,
       Board of Public Works (213) 237-1209.

       Option 12 - Use hydrometallurgical processes to extract metals from sludge. Contact: City
       of Los Angeles Hazardous and Toxic Material Project, Board of Public Works (213) 237-1209.
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        Option 13- Convert sludge to smelter feed. Contact: City of Los Angeles Hazardous and
        Toxic Material Project, Board of Public Works (213) 237-1209.

        Option 14- Remove and recover lead and tin from boards by electrolysis or chemical
        precipitation. Contact: Control Data Corporation and MN Office of Waste Management
        (612) 649-5750.

        Option 15 - Install a closed loop batch treatment system for rinse water to reduce water use
        and waste volume. Costs and Savings: Savings:  $58,460 per year. Capital Investment:
        $210,000. Waste Savings/Reduction: 40,000 gallons per year (40 percent). Contact: Pioneer
        Metal Finishing, Inc., Harry Desoi (609) 694-0400.

        Option 16 - Install an electrolytic cell which recovers 92 percent of dissolved copper in
        drag-out rinses and atmospheric evaporator to recover 95 percent of chromatic acid drag-
        out, and recycle it into chromic acid etch line. Contact: Digital Equipment Corporation and
        Lancy International Consulting Firm, William McLay (412) 452-9360.

        Option 17 - Implement the electrodialysis reversal process for metal salts in wastewater.
        Costs and Savings: Savings: $40,100 per year in operating costs. Contact: Ionics, Inc.,
        Separations Technology Division.

        Option 18 - Oxidize cyanide and remove metallic copper to reduce metal concentrations.
        Contact: Securus, Inc. and DBA Hubbard Enterprises.

V.D.4.        Other Finishing Operations

FINISHING OPERATIONS

Technique -  Training and  Supervision

        Option 1 - Always use proper spraying techniques.

        Option 2 - Improved paint quality, work efficiency, and lower vapor emissions can be
        attained by formal training of operators.

        Option 3 - Avoid buying excess finishing material at one time due to its short shelf-life.

Technique -  Production Planing  and  Sequencing

        Option  1 - Use the correct spray gun for particular applications:
        •   conventional air spray gun for thin-film-build requirements
        •   airless gun for heavy film application
        •   air assisted airless spray gun for a wide range of fluid output.

        Option  2 - Preinspect parts to prevent painting of obvious rejects.
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Technique  - Process or  Equipment Modification

       Option 1 - Ensure the spray gun ak supply is free of water, oil, and dirt.

       Option 2 - Replace galvanizing processes requiring high temperature and flux with one that
       is low temperature and does not require flux. Costs and Savings: Capital Investment:
       $900,000. Annual Savings: 50 percent (as compared to conventional galvanizing). Product
       Throughput Information:  1,000 kg/h.

       Option 3 - Investigate use of transfer methods that reduce material loss such as:
       •   dip and flow coating
       •   electrostatic spraying
       •   electrodeposition.

       Option 4 - Change from conventional ak spray to an electrostatic finishing system. Costs
       and Savings: $15,000 per year. Payback Period: less than 2 years.

       Option 5 - Use solvent recovery or incineration to reduce the emissions of volatile organics
       from curing ovens. Costs and Savings: Annual Savings: $400,000.

       Option 6 - Regenerate anodizing and alkaline silking baths with contemporary
       recuperation of aluminum salts. Costs and Savings: $0.20 per meter of aluminum treated per
       year.  Waste Throughput Information: based on an example plant that previously disposed
       180,000 liters of acid solution per year at $0.07 per litre.

Technique - Raw Material  Substitution

       Option 1 - Use alternative coatings for solvent based paints to reduce volatile organic
       materials use and emissions, such as:

       •   high solids coatings (this may require modifying the painting process; including high
            speed/high pressure equipment, a paint distributing system, and paint heaters); Costs
            and Savings:  Waste Savings/Reduction: 30 percent net savings in applied costs per
            square foot.

       •    water based coatings - Costs and Savings: Waste Savings/Reduction:  87 percent drop
            in solvent emissions and decreased hazardous waste production;

       •   powder coatings - Costs and Savings: Capital Investment: $1.5 million. Payback
            Period:  2 years. Example is for a large, wrought iron patio furniture company.

Technique  -  Waste Segregation  and  Separation

       Option 1 - Segregate non-hazardous paint solids from hazardous paint solvents and
       thinners.

Technique  -  Recycling

       Option 1 - Do not dispose of extended shelf life items that do not meet your facility's
       specifications. They may be returned to the manufacturer, or sold or donated as a raw
       material.
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        Option 2 - Recycle metal sludges through metal recovery vendors.

        Option 3 - Use activated carbon to recover solvent vapors, then recover the solvent from the
        carbon by steam stripping, and distill the resulting water/solvent mixture. Costs and
        Savings: Capital Investment: $817,000 (1978).  Waste Savings/Reduction: releases of
        solvent to the atmosphere were reduced from 700 kg/ton of solvent used to 20 kg/ton.

        Option 4 - Regenerate caustic soda etch solution for aluminum by using hydrolysis of sodium
        aluminate to liberate free sodium hydroxide and produce a dry, crystalline hydrate
        alumina byproduct. Costs and Savings: Capital Investment: $260,000. Savings: $169,282
        per year; from reduced caustic soda use, income from the sale of the byproduct, and a
        reduction in the cost of solid waste disposal. Payback Period: 1.54 years.  Product/Waste
        Throughput Information: anodizing operation for which the surface area is processed at a
        rate of 200 M2/hour.

 PAINT CLEANUP

 Technique - Production  Planning and  Sequencing

        Option 1 - Reduce equipment cleaning by painting with lighter colors before darker ones.

        Option 2 - Reuse cleaning solvents for the same resin system by first allowing solids to settle
        out of solution.

        Option 3 - Flush equipment first with dirty solvent before final cleaning with virgin
        solvent.  Costs and Savings: Waste Savings/Reduction:  98 percent; from 25,000 gallons of
        paint cleanup solvents to 400 gallons. Company uses cleanup solvents in formulation of
        subsequent batches.

        Option 4 - Use virgin solvents for final equipment cleaning, then as paint thinner.

        Option 5 - Use pressurized air mixed with a mist of solvent to clean equipment.

Technique -  Raw Material  Substitution

        Option 1 - Replace water-based paint booth filters with dry filters. Dry filters will double
       paint booth life and allow more efficient treatment of wastewater. Costs and Savings:
       Savings per year:  $1,500. Waste Savings/Reduction:  3,000 gallons/year.

Technique - Loss  Prevention and Housekeeping

       Option 1 - To prevent spray gun leakage, submerge only the front end (or fluid control) of the
       gun into the cleaning solvent.

Technique -  Waste Segregation and  Separation

       Option 1 - Solvent waste streams should be kept segregated and free from water
       contamination.
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Technique - Recycling

       Option 1 - Solvent recovery units can be used to recycle spent solvents generated in flushing
       operations.
       •    Install a recovery system for solvents contained in air emissions. Costs and Savings:
            Savings: $1,000 per year.
       •    Use batch distillation to recover isopropyl acetate generated during equipment
            cleanup. Costs and Savings: Payback Period: 2 years.
       •    Use batch distillation to recover xylene from paint equipment cleanup. Costs and
            Savings: Payback Period: 13 months. Savings: $5,000 per year.
       •    Use a small solvent recovery still to recover spent paint thinner from spray gun
            cleanups and excess paint batches. Costs and Savings: Capital Investment:  $6,000 for
            a 15 gallons capacity still. Savings: $3,600 per year in new thinner savings; $5,400 in
            disposal savings. Payback Period:  less than 1 year. Waste Savings/Reduction:  75
            percent (745 gallons of thinner recovered from 1,003 gallons).  Product/Waste
            Throughput Information: 1,500 gallons of spent thinner processed per year.

       •    Install a methyl ethyl ketone solvent recovery system to recover and reuse waste
            solvents.  Costs and Savings: Savings:  $43,000 per year; MEK recovery rate: 20 gallons
            per day, reflecting a 90 percent reduction in waste.

       Option 2 - Arrange an agreement with other small companies to jointly recycle cleaning
       wastes.

V.E.  Pollution Prevention Contacts
              Organization
 Braun Intertec Environmental, Inc.
 Minnesota Office of Waste Management

 Eastside Plating
 Oregon Department of Environmental
 Quality

 North Carolina Department of Natural
 Resources & Community Development
 (Gary Hunt)

 City of Los Angeles Hazardous and Toxic
 Material Project, Board of Public Works
 EPA Hazardous Waste Engineering
 Research Laboratory, Cincinnati, OH
 (Harry Freeman)

 Securus, Inc.
 DBA Hubbard Enterprises
 Technique(s) to Promote Pollution     Telephone
   Prevention Plating Operations        Number

Process or Equipment Modification   (612) 649-5750
Raw Material Substitution

Process or Equipment Modification   (800) 452-4011
Raw Material Substitution
Process or Equipment Modification    (919) 733-7015
Recycling
Process or Equipment Modification
Raw Material Substitution
Recycling

Process or Equipment Modification
Process or Equipment Modification
Recycling
(213) 237-1209
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              Organization


 CALFRAN International, Inc.

 SAIC (Edward R. Saltzberg)

 New Jersey Hazardous Waste Facilities
 Siting Commission, Hazardous Waste
 Source Reduction and Recycling Task Force

 AT&T Bell Laboratories, Princeton, NJ

 Tyndall Air Force Base (Charles
 Carpenter)
 EG&G Idaho (Dan Sucia, Penny Wilcoff,
 John Beller)

 American Etching and Manufacturing,
 Pacoima, CA

 Highland Plating Company, Los Angeles,
 CA

 Control Data Corporation
 Minnesota Office of Waste Management

 Pioneer Metal Finishing, Inc.  (Harry
 Desoi)

Digital Equipment Corporation
 Lancy International Consulting Firm
 (William  McLay)

Ionics, Inc., Separations Technology
Division
  Technique(s) to Promote Pollution
   Prevention Plating Operations

Process or Equipment Modification

Process or Equipment Modification

Process or Equipment Modification



Process or Equipment Modification

Raw Material Substitution
Raw Material Substitution


Raw Material Substitution


Recycling


Recycling


Recycling



Recycling
  Telephone
    Number

 (413) 525-4957
(904) 283-2942

(208) 526-1149
(612) 649-5750


(609) 694-0400


(412) 452-9360
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VI.   SUMMARY OF APPLICABLE FEDERAL STATUTES AND REGULATIONS

            This section discusses the Federal statutes and regulations that may
            apply to this sector.  The purpose of this section is to highlight, and
            briefly describe the applicable Federal requirements, and to provide
            citations for more  detailed information.   The three  following
            sections are included.

            •     Section IV.A contains a general overview of major statutes
            •     Section IV.B  contains a list of regulations specific to this
                  industry
            •     Section IV.C  contains  a  list of pending  and  proposed
                  regulations

            The descriptions within  Section IV are intended solely for general
            information. Depending upon the nature or scope of the activities
            at a particular facility, these summaries may or may not necessarily
            describe all applicable  environmental requirements.  Moreover,
            they do not constitute formal interpretations or clarifications of the
            statutes and regulations. For further information, readers should
            consult the Code of Federal Regulations and other state or  local
            regulatory agencies.  EPA Hotline  contacts are also provided for each
            major statute.
VI.A. General Description of Major Statutes

Resource Conservation And Recovery Act

            The Resource  Conservation And  Recovery Act (RCRA) of 1976
            which amended the Solid Waste  Disposal Act, addresses solid
            (Subtitle D)  and  hazardous  (Subtitle  C) waste  management
            activities.  The Hazardous and Solid Waste Amendments (HSWA)
            of 1984  strengthened RCRA's waste management provisions  and
            added Subtitle I, which governs underground storage tanks (USTs).

            Regulations promulgated pursuant to Subtitle C  of RCRA (40 CFR
            Parts  260-299)  establish  a  "cradle-to-grave" system governing
            hazardous waste from the point of generation to disposal.  RCRA
            hazardous wastes  include  the specific materials  listed  in the
            regulations (commercial chemical  products, designated  with the
            code "P" or "U"; hazardous wastes from specific industries/sources,
            designated with the code "K"; or hazardous wastes from non-
            specific  sources, designated with the code "F") or materials which
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             exhibit a hazardous waste characteristic (ignitibility,  corrosivity,
             reactivity, or toxicity and designated with the code "D").

             Regulated entities that generate  hazardous waste are subject to
             waste accumulation, manifesting, and recordkeeping standards.
             Facilities that treat, store, or dispose of hazardous waste must obtain
             a permit, either from EPA or from a State agency  which EPA has
             authorized to implement  the  permitting  program.   Subtitle C
             permits contain general facility standards such as contingency plans,
             emergency procedures, recordkeeping and reporting requirements,
             financial assurance  mechanisms,  and unit-specific  standards.
             RCRA also contains provisions (40 CFR Part  264 Subpart S  and
             §264.10) for conducting corrective actions which govern the cleanup
             of releases  of  hazardous waste or constituents  from solid waste
             management units at RCRA-regulated facilities.

             Although RCRA is a Federal statute, many States implement the
             RCRA program.  Currently,  EPA has  delegated its authority to
             implement various provisions of RCRA to 46 of the  50 States.

             Most RCRA requirements are not industry specific but apply to  any
             company that  transports, treats, stores, or disposes of hazardous
             waste. Here are some important RCRA regulatory requirements:

             •     Identification of Solid  and  Hazardous Wastes (40 CFR Part
                  261)  lays out the procedure every generator should follow to
                  determine whether  the material created is considered a
                  hazardous waste, solid waste, or is exempted from regulation.

             •     Standards for Generators of Hazardous Waste (40 CFR Part
                  262)  establishes the responsibilities  of hazardous waste
                  generators including obtaining an ID  number, preparing a
                  manifest, ensuring proper packaging and  labeling, meeting
                  standards for waste  accumulation units,  and recordkeeping
                  and  reporting requirements.  Generators can  accumulate
                  hazardous waste for up to 90 days (or 180 days depending on
                  the amount of waste generated) without obtaining a permit.

             •     Land Disposal Restrictions (LDRs) are regulations prohibiting
                  the disposal of hazardous waste  on land  without prior
                  treatment.  Under the LDRs (40  CFR 268),  materials must
                  meet  land disposal  restriction (LDR) treatment standards
                  prior  to  placement in a RCRA land disposal unit (landfill,
                  land treatment unit, waste  pile, or surface impoundment).
                  Wastes subject to the LDRs include solvents, electroplating
                  wastes, heavy metals, and acids.  Generators of waste subject
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                  to the LDRs must provide  notification of such to the
                  designated TSD facility to ensure proper treatment prior to
                  disposal.

            •     Used Oil Management Standards (40 CFR Part 279) impose
                  management   requirements  affecting   the   storage,
                  transportation, burning, processing, and  re-refining of the
                  used oil.   For parties that  merely  generate  used oil,
                  regulations  establish  storage  standards.   For  a party
                  considered a used oil marketer (one who generates and sells
                  off-specification used oil directly to a used oil  burner),
                  additional tracking and paperwork requirements  must be
                  satisfied.

            •     Tanks and Containers used to store hazardous waste with a
                  high volatile organic concentration must meet emission
                  standards under RCRA. Regulations (40  CFR Part 264-265,
                  Subpart CC) require generators to test the waste to determine
                  the concentration of the waste, to satisfy tank and container
                  emissions standards,  and to inspect and monitor regulated
                  units.  These regulations apply to all facilities who store such
                  waste, including generators  operating under the 90-day
                  accumulation rule.

            •     Underground Storage  Tanks (USTs) containing  petroleum
                  and hazardous substance are  regulated under Subtitle I of
                  RCRA.  Subtitle I regulations (40 CFR Part 280) contain tank
                  design and  release  detection requirements, as  well as
                  financial responsibility and corrective action standards  for
                  USTs.   The  UST  program also establishes increasingly
                  stringent standards,  including upgrade requirements  for
                  existing tanks, that must be met by 1998.

            •     Boilers and Industrial  Furnaces (BIFs) that use or burn fuel
                  containing hazardous waste must comply with strict design
                  and operating standards.  BIF regulations (40 CFR Part 266,
                  Subpart H)  address unit  design, provide performance
                  standards, require emissions monitoring, and restrict the type
                  of waste that may be burned.

            EPA's RCRA/Superfund/UST  Hotline,  at (800) 424-9346,  responds
            to  questions  and  distributes  guidance   regarding   all  RCRA
            regulations.  The RCRA Hotline operates  weekdays from 8:30 a.m.
            to 7:30  p.m., EST, excluding Federal holidays.
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 Comprehensive Environmental Response, Compensation, And Liability Act

            The Comprehensive Environmental Response, Compensation, and
            Liability Act (CERCLA), a 1980 law commonly  known as Superfund,
            authorizes EPA to respond  to releases, or  threatened releases, of
            hazardous substances  that may endanger public health, welfare, or
            the environment.   CERCLA also enables EPA to force parties
            responsible for environmental contamination  to clean it up or to
            reimburse the Superfund for response costs incurred by EPA.  The
            Superfund Amendments and Reauthorization Act (SARA) of 1986
            revised various sections of CERCLA, extended the taxing authority
            for the Superfund, and created a free-standing law, SARA Title III,
            also known as the Emergency Planning and Community Right-to-
            Know Act (EPCRA).

            The CERCLA hazardous substance release reporting regulations (40
            CFR Part 302) direct  the person in charge of a facility to report to the
            National Response Center (NRC) any environmental release of a
            hazardous substance which  exceeds a  reportable quantity.
            Reportable quantities are defined and listed in 40 CFR § 302.4.  A
            release report may trigger a response by EPA, or by one or more
            Federal or State emergency response authorities.

            EPA implements  hazardous substance responses according to
            procedures outlined  in the National Oil and Hazardous Substances
            Pollution Contingency Plan  (NCP) (40  CFR Part 300).  The NCP
            includes provisions  for permanent cleanups,  known as remedial
            actions, and  other  cleanups referred  to  as "removals."   EPA
            generally  takes remedial  actions  only  at  sites on the National
            Priorities List (NPL), which currently includes approximately 1300
            sites.  Both EPA and  states  can  act at  other  sites;  however, EPA
            provides responsible parties the opportunity  to conduct  removal
            and remedial actions  and encourages  community involvement
            throughout the Superfund response process.

            EPA's  RCRA/Superfund/UST Hotline, at (800) 424-9346,  answers
            questions  and references  guidance  pertaining  to  the  Superfund
            program.  The  CERCLA Hotline operates  weekdays from 8:30 a.m. to
            7:30 p.m., EST, excluding Federal holidays.

Emergency Planning And Community Right-To-Know Act

            The Superfund Amendments and Reauthorization Act (SARA) of
            1986  created  the Emergency Planning and Community Right-to-
            Know  Act (EPCRA, also known  as SARA  Title  III), a statute
            designed to  improve  community access  to  information  about
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            chemical hazards and to facilitate the  development of chemical
            emergency response plans by State and local governments. EPCRA
            required  the  establishment of State  emergency  response
            commissions  (SERCs),  responsible for  coordinating certain
            emergency response activities  and for appointing local emergency
            planning committees (LEPCs).

            EPCRA and the EPCRA regulations (40 CFR Parts 350-372) establish
            four types of reporting  obligations for facilities which store or
            manage specified chemicals:

            «     EPCRA §302 requires facilities to notify the SERC and LEPC of
                  the presence of any "extremely hazardous substance" (the list
                  of such substances is in 40 CFR Part 355, Appendices A and B)
                  if it has such substance in excess of the substance's threshold
                  planning  quantity, and directs the  facility to appoint an
                  emergency response coordinator.

            •     EPCRA §304 requires the facility to notify the SERC and the
                  LEPC in  the  event of  a release  exceeding the  reportable
                  quantity of a CERCLA hazardous substance or an EPCRA
                  extremely hazardous substance.

            •     EPCRA §§311 and 312 require a facility at which a hazardous
                  chemical, as defined by the Occupational Safety and Health
                  Act, is present in an amount exceeding a specified threshold
                  to submit to  the  SERC, LEPC, and local fire department
                  material safety data sheets  (MSDSs) or lists of MSDSs and
                  hazardous chemical inventory forms (also known as Tier  I
                  and H forms).  This information helps  the local government
                  respond in the event of a spill or release of the chemical.

            •     EPCRA §313 requires manufacturing facilities included in SIC
                  codes 20 through 39, which have ten or more employees, and
                  which manufacture, process, or use specified  chemicals in
                  amounts  greater than  threshold  quantities, to  submit an
                  annual toxic chemical release report.  This report, commonly
                  known as the Form R, covers releases  and transfers of toxic
                  chemicals to  various facilities and environmental media, and
                  allows EPA to compile  the national Toxic Release Inventory
                  (TRI) database.


            All information submitted pursuant  to  EPCRA  regulations  is
            publicly accessible, unless protected by a trade secret claim.
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             EPA's  EPCRA Hotline, at (800) 535-0202, answers  questions and
             distributes  guidance  regarding  the  emergency  planning  and
             community  right-to-know  regulations.    The  EPCRA  Hotline
             operates'weekdays from  8:30  a.m.  to  7:30 p.m.,  EST, excluding
             Federal  holidays.
 Clean Water Act
             The primary objective of the Federal Water Pollution Control Act,
             commonly referred to as the Clean Water Act (CWA), is to restore
             and maintain the chemical, physical, and biological integrity of the
             nation's surface  waters.   Pollutants regulated  under  the CWA
             include "priority" pollutants, including various toxic pollutants;
             "conventional"  pollutants, such  as biochemical oxygen demand
             (BOD), total suspended  solids (TSS), fecal coliform, oil and grease,
             and  pH;  and  "non-conventional"  pollutants, including any
             pollutant not identified as either conventional or priority.

             The CWA  regulates both direct and  indirect discharges.  The
             National  Pollutant Discharge  Elimination  System  (NPDES)
             program (CWA §402)  controls direct  discharges  into  navigable
             waters.  Direct discharges or "point source" discharges are from
             sources such as pipes and sewers. NPDES permits, issued by either
             EPA or an authorized  State  (EPA has  presently authorized forty
             States to administer the NPDES program),  contain industry-specific,
             technology-based and/or water quality-based limits, and establish
             pollutant monitoring and  reporting requirements.  A  facility that
             intends to  discharge into the nation's waters must obtain a permit
             prior to initiating its discharge.  A  permit applicant must provide
             quantitative analytical  data  identifying  the types of pollutants
             present in the facility's effluent.  The permit will then set forth the
             conditions and effluent limitations under which  a  facility may
             make a discharge.

             A NPDES permit may also include discharge limits based on Federal
             or State water  quality criteria or standards, that were designed to
             protect designated uses of-surface waters, such as supporting aquatic
             life or  recreation.   These  standards,  unlike the technological
             standards,  generally do  not  take into account technological
             feasibility or costs. Water  quality criteria and standards vary from
             State to State, and site to site, depending on the  use classification of
             the receiving body of water.  Most States follow EPA guidelines
            which propose aquatic life and human health criteria for many of
            the 126 priority pollutants.
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            Storm Water Discharges

            In  1987 the CWA was amended to require EPA  to  establish a
            program to  address storm water  discharges.  In  response, EPA
            promulgated  the  NPDES storm  water permit  application
            regulations.  Storm water discharge associated with industrial
            activity means the discharge from any conveyance which is used for
            collecting and conveying storm water and which is directly related
            to manufacturing, processing or raw materials storage areas at an
            industrial plant (40 CFR 122.26(b)(14)).  These regulations require
            that facilities with the following storm water discharges apply for a
            NPDES permit:  (1) a discharge associated with industrial activity; (2)
            a discharge from a large or medium municipal storm sewer system;
            or (3) a discharge which EPA or the State determines  to contribute to
            a violation of a water quality standard or is a significant contributor
            of pollutants to waters of the United States.

            The term "storm water discharge associated with industrial activity"
            means a storm water discharge  from one of 11 categories  of
            industrial activity defined at 40 CFR 122.26.  Six of the categories are
            defined by SIC codes  while the  other  five are identified through
            narrative descriptions of the  regulated industrial  activity.  If the
            primary SIC code of the facility is one of those identified in the
            regulations,  the facility is subject to the storm water  permit
             application requirements.  If any activity at a facility is covered by
             one  of the five narrative categories, storm water discharges from
             those areas where the activities  occur are  subject  to storm water
             discharge permit application requirements.

             Those facilities/activities that are subject to storm water discharge
             permit  application  requirements  are  identified  below.   To
             determine  whether a  particular facility falls within one of these
             categories, the regulation should be consulted.

             Category i:  Facilities subject to storm water effluent guidelines, new
             source performance standards, or toxic pollutant effluent standards.

             Category ii: Facilities classified as SIC 24-lumber and wood products
             (except wood kitchen cabinets); SIC 26-paper and allied products
             (except paperboard containers and products); SIC 28-chemicals and
             allied products (except drugs and paints); SIC 29-petroleum refining;
             and SIC 311-leather tanning and  finishing.
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             Category iii: Facilities classified as SIC 10-metal mining; SIC 12-coal
             mining;  SIC 13-oil and  gas extraction;  and SIC 14-nonmetallic
             mineral  mining.

             Category iv:  Hazardous waste  treatment,  storage,  or disposal
             facilities.

             Category v: Landfills, land application sites, and open dumps that
             receive or have received industrial wastes.

             Category vi: Facilities classified  as  SIC 5015-used motor vehicle
             parts; and SIC 5093-automotive scrap and waste material recycling
             facilities.

             Category vii: Steam electric power generating facilities.

             Category viii:  Facilities classified  as SIC 40-railroad transportation;
             SIC  41-local  passenger  transportation;  SIC  42-trucking  and
             warehousing (except public warehousing and storage); SIC 43-U.S.
             Postal Service; SIC 44-water transportation; SIC 45-transportation by
             air; and SIC 5171-petroleum bulk storage stations and terminals.

             Category ix: Sewage treatment works.

             Category x:  Construction activities except operations that result in
             the disturbance of less than five acres of total land area.

             Category xi: Facilities classified as SIC 20-food and kindred products;
             SIC 21-tobacco products; SIC 22-textile mill products; SIC 23-apparel
             related products; SIC 2434-wood  kitchen  cabinets manufacturing;
             SIC 25-furniture and  fixtures; SIC 265-paperboard containers  and
             boxes; SIC 267-converted  paper and paperboard products; SIC 27-
             printing,  publishing, and allied industries; SIC 283-drugs; SIC 285-
             paints, varnishes,  lacquer, enamels,  and allied products; SIC 30-
             rubber and  plastics; SIC  31-leather and leather products (except
             leather and tanning and finishing); SIC 323-glass products; SIC 34-
             fabricated metal products (except fabricated structural metal); SIC 35-
             industrial and commercial machinery and computer  equipment;
             SIC 36-electronic and other electrical equipment and components;
             SIC 37-transportation equipment (except ship and boat building and
             repairing);  SIC  38-measuring,  analyzing,  and  controlling
             instruments; SIC 39-miscellaneous manufacturing industries; and
             SIC 4221-4225-public warehousing and storage.
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            Pretreatment Program

            Another type of discharge that is regulated by the CWA is one that
            goes to a publicly-owned treatment works (POTWs). The national
            pretreatment program (CWA §307(b)) controls the indirect discharge
            of pollutants to POTWs by "industrial users."  Facilities regulated
            under §307(b) must meet certain pretreatment standards. The goal
            of the  pretreatment program  is to protect municipal wastewater
            treatment plants  from damage that may occur when hazardous,
            toxic, or other wastes  are  discharged into a  sewer system and to
            protect the quality of sludge generated by these plants. Discharges to
            a POTW are regulated primarily by the POTW itself, rather than the
            State or EPA.

            EPA has developed technology-based standards for industrial users
            of POTWs.  Different standards apply to existing and new sources
            within  each  category.    "Categorical"  pretreatment standards
            applicable to an industry on a nationwide basis are developed by
            EPA.  In addition, another kind of pretreatment standard,  "local
            limits," are developed by the POTW in order to assist the POTW in
            achieving the effluent limitations in its NPDES permit.

            Regardless of whether  a State is authorized to implement either the
            NPDES  or  the pretreatment program,  if  it develops its  own
            program, it may  enforce requirements  more stringent than Federal
            standards.

            EPA's  Office of Water, at (202) 260-5700, will direct callers with
            questions  about the CWA to the appropriate EPA office.  EPA also
            maintains a  bibliographic database of Office  of Water publications
            which  can be  accessed through  the Ground Water and  Drinking
            Water resource center, at (202) 260-7786.
 Safe Drinking Water Act
            The Safe Drinking Water Act (SDWA) mandates that EPA establish
            regulations  to protect  human  health from  contaminants  in
            drinking water.  The law authorizes EPA to  develop national
            drinking water standards and to create  a joint Federal-State system
            to ensure compliance with these standards.  The SDWA also directs
            EPA to protect underground sources of drinking water through the
            control of underground injection of liquid wastes.

            EPA has developed primary and secondary  drinking  water
            standards under its SDWA authority.  EPA and authorized States
            enforce  the  primary  drinking  water standards,  which are,
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            contaminant-specific concentration limits that apply  to  certain
            public drinking water supplies. Primary drinking water standards
            consist of maximum contaminant level goals (MCLGs), which are
            non-enforceable health-based  goals, and  maximum contaminant
            levels (MCLs), which are enforceable limits  set as close to MCLGs as
            possible, considering cost and feasibility of attainment.

            The SDWA Underground Injection Control (UIC) program (40 CFR
            Parts 144-148)  is a  permit program which protects underground
            sources of drinking water by  regulating  five classes of injection
            wells.   UIC permits include  design, operating, inspection, and
            monitoring  requirements.  Wells used to  inject hazardous wastes
            must also comply with RCRA  corrective action standards in order
            to be granted a RCRA permit, and must meet applicable RCRA land
            disposal restrictions standards.   The  UIC permit  program is
            primarily State-enforced, since EPA has authorized all but a few
            States to administer the program.

            The SDWA  also provides for a Federally-implemented Sole Source
            Aquifer program, which  prohibits Federal  funds  from  being
            expended on projects that may contaminate the sole  or principal
            source  of  drinking  water  for a  given area, and  for a  State-
            implemented Wellhead  Protection program, designed to protect
            drinking water wells and drinking water recharge areas.

            EPA's  Safe  Drinking Water  Hotline, at (800) 426-4791,  answers
            questions and distributes guidance pertaining  to SDWA  standards.
            The  Hotline operates from  9:00  a.m.  through  5:30  p.m., EST,
            excluding  Federal holidays.
Toxic Substances Control Act
            The Toxic Substances Control Act (TSCA) granted EPA authority to
            create a regulatory framework to collect data on chemicals in order
            to evaluate, assess, mitigate, and control risks which may be posed
            by their manufacture, processing, and use.  TSCA provides a variety
            of control methods to prevent chemicals from posing unreasonable
            risk.

            TSCA standards may apply at any point during a chemical's  life
            cycle.   Under  TSCA §5, EPA has established  an inventory of
            chemical substances.  If a chemical is not already on the inventory,
            and has not been excluded by TSCA, a  premanufacture  notice
            (PMN) must be submitted to EPA prior to  manufacture or import.
            The PMN must identify  the chemical  and  provide available
            information on  health and environmental effects.  If available data
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            are not sufficient to evaluate the chemical's effects, EPA can impose
            restrictions pending the development of information on its health
            and environmental effects.  EPA can also restrict significant new
            uses of chemicals based upon factors such as the projected volume
            and use of the chemical.

            Under TSCA §6, EPA can ban the manufacture  or distribution in
            commerce, limit the use, require labeling, or place other restrictions
            on chemicals that pose unreasonable risks. Among the chemicals
            EPA regulates under §6 authority are asbestos, chlorofluorocarbons
            (CFCs), and polychlorinated biphenyls (PCBs).

            EPA's TSCA  Assistance  Information  Service,  at (202) 554-1404,
            answers  questions  and  distributes  guidance  pertaining  to  Toxic
            Substances Control Act standards.   The Service operates from  8:30
            a.m. through 4:30 p.m., EST, excluding Federal holidays.
 Clean Air Act
            The Clean Air Act (CAA) and its amendments, including the Clean
            Air Act Amendments (CAAA) of 1990, are designed to "protect and
            enhance the nation's  air resources so as to promote  the public
            health and welfare and the productive capacity of the population."
            The CAA consists of six sections, known as Titles, which direct EPA
            to establish national standards for ambient air quality and for EPA
            and the States to implement, maintain, and enforce these standards
            through  a variety of mechanisms.   Under  the  CAAA, many
            facilities will be required to obtain permits for the first time.  State
            and local governments oversee, manage, and enforce many of the
            requirements of the CAAA.  CAA regulations appear at 40 CFR
            Parts 50-99.

            Pursuant  to  Title I  of the CAA, EPA  has established  national
            ambient air quality standards (NAAQSs) to  limit levels of "criteria
            pollutants,"  including carbon monoxide, lead, nitrogen  dioxide,
            particulate matter, ozone, and sulfur dioxide.  Geographic areas that
            meet NAAQSs  for a  given pollutant are classified  as attainment
            areas; those  that do not  meet NAAQSs  are classified  as non-
            attainment areas. Under §110 of the CAA, each State must develop
            a State Implementation Plan  (SIP) to identify sources  of air
            pollution  and to determine what reductions are required to meet
            Federal air quality standards.

            Title I also authorizes EPA to establish  New Source Performance
            Standards (NSPSs),  which  are nationally  uniform emission
             standards for new  stationary  sources  falling within particular
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             industrial categories.  NSPSs are based on the pollution control
             technology available to that category of industrial source but allow
             the affected industries the flexibility to devise a cost-effective means
             of reducing emissions.

             Under Title I,  EPA establishes and enforces National Emission
             Standards  for Hazardous  Air Pollutants  (NESHAPs), nationally
             uniform standards  oriented  towards   controlling  particular
             hazardous  air pollutants (HAPs).  Title III of the CAAA further
             directed EPA to develop a list of sources that emit any of 189 HAPs,
             and to develop  regulations  for these categories of sources. To date
             EPA  has listed 174 categories and developed a schedule for the
             establishment of emission standards.  The emission standards will
             be developed  for  both new and existing sources  based on
             "maximum  achievable control  technology" (MACT).  The MACT is
             defined as  the control technology achieving the maximum degree
             of reduction in  the emission of the HAPs, taking into account cost
             and other factors.

             Title II of the CAA pertains to mobile sources, such as cars, trucks,
             buses, and  planes.  Reformulated gasoline, automobile pollution
             control devices,  and vapor recovery nozzles on gas pumps are a few
             of the mechanisms  EPA uses to  regulate mobile  air emission
             sources.
            Title IV establishes a sulfur dioxide emissions program designed to
            reduce the  formation of acid rain.  Reduction of  sulfur dioxide
            releases will be  obtained by granting to certain sources limited
            emissions allowances, which, beginning in 1995, will be set below
            previous levels of sulfur dioxide releases.

            Title V of the CAAA of 1990 created a permit program for all "major
            sources" (and certain other sources) regulated under the CAA. One
            purpose of the operating permit is to include in a single document
            all air  emissions requirements that apply to a given facility.  States
            are developing the permit programs in accordance  with guidance
            and regulations from EPA. Once a State program is approved by
            EPA, permits will be issued and monitored by that State.

            Title VI is intended to protect stratospheric  ozone by phasing out
            the manufacture of ozone-depleting chemicals and restrict their use
            and distribution.  Production of Class I substances, including 15
            kinds of chlorofluorocarbons (CFCs), will be phased out entirely by
            the year 2000, while certain hydrochlorofluorocarbons (HCFCs) will
            be phased out by 2030.
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            EPA's  Control  Technology  Center,  at  (919)  541-0800,  provides
            general  assistance and information  on  CAA  standards.    The
            Stratospheric  Ozone  Information Hotline,  at  (800)  296-1996,
            provides general  information about regulations promulgated under
            Title VI of the CAA, and EPA's EPCRA  Hotline,  at (800) 535-0202,
            answers  questions about accidental release  prevention under  CAA
            §112(r).   In addition,  the  Technology  Transfer  Network Bulletin
            Board  System (modem  access (919) 541-5742)) includes recent CAA
            rules, EPA guidance documents, and updates of EPA activities.
            This section discusses the Federal regulations that may apply to this
            sector.   The purpose of this section is to highlight, and briefly
            describe the applicable Federal requirements so  that the reader is
            aware of these requirements. The section provides a summary of
            each major environmental statute, and a description of regulations
            that may specifically apply to the profiled industry.  Some profiles
            also provide information regarding  current rulemaking activity
            that might specifically impact this sector. The descriptions within
            Section  VI  are  intended  solely  for guidance.  No  statutory  or
            regulatory requirements are in any way  altered by any statement(s)
            contained herein.  For more in-depth information,  readers should
            consult the United States Code and the Code of Federal Regulations
            as well as State or local regulatory agencies.  EPA Hotline contacts
            are also provided for each major statute.


VLB.  Industry Specific Regulations

            A number of statutes and regulations affect the metal  fabrication
            and finishing industry.   The electroplating and  metal finishing
            pretreatment standards promulgated under  the Clean  Water  Act
            regulate the chemicals in wastewater, the Clean Air  Act regulates air
            emissions,  and the Resource Conservation and Recovery  Act
            regulates hazardous waste generation, transportation, treatment,
            storage, and disposal. Each is discussed briefly below.

Clean Water Act (CWA)

            Two  Clean Water Act regulations affect the fabricated  metal
            products industry (SIC 34): the Effluent Guidelines and Standards
             for Metal Finishing (40 CFR Part 433) and the Effluent Guidelines
             and Standards for Electroplating (40 CFR Part 413).  The regulations
             targeting the electroplating industry  were issued  before those
             targeting the metal finishing industry as a whole.   Companies
             regulated by the electroplating standards (40 CFR Part 413) before the
             metal  finishing standards (40 CFR Part 433) were promulgated,
             become subject to the requirements of the metal  finishing standards
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             when (or if) they make modifications to their facility's operating
             functions (e.g., facility, equipment, process  modifications).   If
             companies made no such modifications, they remain regulated by
             the electroplating standards.  All new facilities are subject to the
             standards set forth in 40 CFR Part 433.

             The Effluent Guidelines and Standards for Metal Finishing (40 CFR
             Part 433) are applicable to wastewater generated by any  of these
             operations:

                   Electroplating
                   Electroless Plating
                   Anodizing
                   Coating
                   Chemical Etching and Milling
                   Printed Circuit Board Manufacturing.

             If any of the above processes are performed, the metal finishing
             standards will also apply to discharges from 40 additional processes,
             including:  cleaning, polishing, shearing, hot dip coating, solvent
             degreasing, painting, etc.

             The standards include  daily maximums and maximum  monthly
             average  concentration limitations.  The standards  are based on
             milligrams per  square meter  of operation  and determine  the
             amount of wastewater pollutants from various operations that may
             be discharged. The uniformity in standards meets  industry requests
             for equivalent limits for process lines often found together.  The
             metal finishing standards also reduce the need to use the Combined
             Wastestream Formula.

             Specific  pretreatment standards  may  also  apply to wastewater
             discharges  from  other metal finishing operations.   The more
             specific standards will apply to those metal finishing wastestreams
             which  appear to be covered by both standards.  The requirements in
             the following regulations take precedence over those contained in
             the general metal finishing regulation:

             •     Iron and Steel Manufacturing (40 CFR Part 420)

             •     Battery Manufacturing (40 CFR Part 461)

             •     Plastic Molding and Forming (40 CFR Part 463)

             •     Coil Coating (40 CFR Part 465)

             •     Porcelain Enameling (40 CFR Part 466)
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            •     Aluminum Forming (40 CFR Part 467)

                  Copper Forming (40 CFR Part 468)

            •     Electrical and Electronic Components (40 CFR Part 469)

                  Nonferrous Forming (40 CFR Part 471)

            «     Lead-Tin-Bismuth Forming Category (40 CFR Part 471,
                  Subpart A)

            •     Zinc Forming Subcategory (40 CFR Part 471, Subpart H).

            The Effluent Guidelines and Standards for Electroplating  (40 CFR
            Part 413)  cover  wastewater  dischargers  from  electroplating
            operations, in which metal is electroplated on any  basis material,
            and to  related metal finishing  operations.  As stated previously,
            facilities regulated by the electroplating standards may become
            subject  to the metal finishing standards if they make modifications
            to  their facility's operating  functions (e.g., facility,  equipment,
            process modifications).   Independent printed  circuit  board
            manufacturers are defined as facilities which manufacture printed
            circuit  boards principally for  sale  to other  companies.   These
            facilities remain subject only to the electroplating standards (40 CFR
            Part 413), primarily to minimize the economic impact  to  these
            relatively small facilities.  Also excluded  from the metal finishing
            regulations are facilities which perform metallic  platemaking and
            gravure cylinder preparation  conducted  within  printing and
            publishing facilities.

            Operations similar to electroplating which are  specifically exempt
            from coverage under the electroplating standards include:

             •    Continuous strip electroplating conducted within iron and
                  steel manufacturing facilities (40 CFR Part 420)

             •    Electrowinning  and electrorefining  conducted  as  part  of
                  nonferrous metal smelting and refining (40 CFR Part 421)

             •     Electrodeposition   of   active   electrode   materials,
                   electroimpregnation, and electroforming conducted as part of
                   battery manufacturing (40 CFR Part 461)

             •     Metal surface preparation and conversion coating conducted
                   as part of coil coating (40 CFR Part 465)

             •     Metal surface  preparation  and immersion  plating  or
                   electroless plating conducted as a part of porcelain enameling
                   (40 CFR Part 466)
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                  Metallic platemaking and gravure  cylinder  preparation
                  conducted within printing and publishing facilities

                  Surface  treatment "including  anodizing  and  conversion
                  coating conducted as part of aluminum forming (40 CFR Part
                  467).
Clean Air Act
            The following standards and requirements promulgated under the
            CAA apply to metal finishing processes:

            •     National  Emission  Standards, for  Chromium Emissions
                  From Hard and Decorative Chromium Electroplating and
                  Chromium Anodizing Tanks (40 CFR Parts 9 and 63, Subpart
                  N, 60 FR 498, January 1995)

            •     Standards  of  Performance  for Surface  Coating of Metal
                  Furniture (40 CFR Part 60, Subpart EE)

            •     Standards of Performance for Automobile and Light-Duty
                  Truck Surface  Coating Operations (40 CFR Part 60,  Subpart
                  MM)

            •     Standards of Performance for Industrial Surface Coatings:
                  Large Appliances (40 CFR Part 60, Subpart SS)

            •     Standards of Performance for Metal Coil Surface Coating (40
                  CFR Part 60, Subpart TT)

            •     Standards  of  Performance for the Beverage Can  Surface
                  Coating Industry (40 CFR Part 60, Subpart WW)

            •     Standards of Performance  for Industrial Surface Coating:
                  Surface Coating of Plastic Parts for Business Machines (40
                  CFR Part 60, Subpart TTT).


            These standards and requirements, although to varying degrees,
            regulate the discharge of volatile organic chemicals (VOCs).

Resource Conservation and Recovery Act (RCRA)

            The greatest  quantities of  RCRA listed waste and characteristic
            hazardous waste present in the fabricated metal products industry
            are identified in Exhibit  33.   For more information on RCRA
            hazardous waste, refer to 40 CFR Part 261.
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                                        Exhibit 33
            Hazardous Wastes Relevant to the Metal Finishing Industry
 EPA Hazardous
   Waste No.
                            Hazardous Waste
D006 (cadmium)
D007 (chromium)
D008 (lead)
D009 (mercury)
DOW (selenium)
D011 (silver)
Wastes which are hazardous due to the characteristic of toxicity for each of
the constituents.
F001
Halogenated solvents used in degreasing:  tetrachloroethylene, methylene
chloride, 1,1,1-trichloroethane, carbon tetrachloride, and chlorinated
fluorocarbons; all spent solvent mixtures/blends used in degreasing containing,
before use, a total of 10 percent or more (by volume) of one or more of the above
halogenated solvents or those solvents listed in F002, F004, and F005; and still
bottoms from the recovery of these spent solvents and spent solvent mixtures.
F002
Spent halogenated solvents; tetrachloroethylene, methylene chloride,
trichlorethylene, 1,1,1-trichloroethane chlorobenzene, l,l,2-trichloro-l,2,2-
trifluoroethane, ortho-dichlorobenzene, trichlorofluoromethane, and 1,1,2-
trichloroethane; all spent solvent mixtures/blends containing, before use, one
or more of the above halogenated solvents or those listed in F001, F004, F005;
and still bottoms from the recovery of these spent solvents and spent solvent
mixtures.                                               	
F003
Spent non-halogenated solvents: xylene, acetone, ethyl acetate, ethyl benzene,
ethyl ether, methyl isobutyl ketone, n-butyl alcohol, cyclohexanone, and
methanol; all spent solvent mixtures/blends containing, before use, only the
above spent non-halogenated solvents; and all spent solvent mixtures/blends
containing, before use, one or more of the above non-halogenated solvents, and,
a total of 10 percent or more (by volume) of one of those solvents listed in F001,
F002, F004, F005; and still bottoms from the recovery of these spent solvents
and spent solvent mixtures
F004
Spent non-halogenated solvents: cresols and cresylic acid, and nitrobenzene;
all spent solvent mixtures/blends containing, before use, a total of 10 percent or
more (by volume) of one or more of the above non-halogenated solvents or those
solvents listed in F001, F002, and F005; and still bottoms from the recovery of
these spent solvents and spent solvent mixtures.
F005
Spent non-halogenated solvents: toluene, methy ethyl ketone, carbon
disulfide, isobutanol, pyridine, benzene, 2-ethoxyethanol, and 2-nitropropane;
all spent solvent mixtures/blends containing, before use, a total of 10 percent or
more (by volume) of one or more of the above non-halogenated solvents or those
solvents listed in F001, F002, or F004; and still bottoms from the recovery of
these spent solvents and spent solvents mixtures
F006
Wastewater treatment sludges from electroplating operations except from the
following processes: (1) sulfuric acid anodizing of aluminum; (2) tin plating on
carbon steel; (3) zinc plating (segregated basis) on carbon steel; (4) aluminum or
zinc-aluminum plating on carbon steel; (5) cleaning/stripping associated with
tin, zinc, and aluminum plating on carbon steel; and (6) chemical etching and
nulling of aluminum,
 F007
 Spent cyanide plating bath solutions from electroplating operations.
 F008
•_^IM^HH«^^^^^^^^^^^^^—II II                       	
Plating bath residues from the bottom of plating baths from electroplating
operations where cyanides are used in the process.
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                                  Exhibit 33
          Hazardous Wastes Relevant to the Metal Finishing Industry
EPA Hazardous
Waste No.
F009
F010
F011
F012
F019
K090
K091
Hazardous Waste
Spent stripping and cleaning bath solutions from electroplating operations
where cyanides are used in the process.
Quenching bath residues from oil baths from metal heat treating operations
where cyanides are used in the process.
Spent cyanide solutions from salt bath pot cleaning from metal heat treating
operations.
Quenching wastewater treatment sludges from metal heat treating operations
where cyanides are used in the process.
Wastewater treatment sludges from the chemical conversion coating of
aluminum from zirconium phosphating is an exclusive conversion coating
process.
Emission control dust or sludge from ferrochromiumsilicon production
(ferroalloy industry).
Emission control dust or sludge from ferrochromium production (ferroalloy
industry).
  source: bustmnawe industry: Promoting btratenc bnvironmental Protection in the Industrial Sector. Phase 1
                           Report. U.S. EPA, OERR, June 1994.
VI.C. Pending and Proposed Regulatory Requirements

Clean Water Act (CWA)

             The effluent guidelines and standards for Electroplaters (40 CFR Part
             413) and Metal Finishers  (40 CFR Part 433) are currently under
             review.  EPA is also currently developing effluent guidelines and
             standards for the  metal products and machinery industry (40 CFR
             Part 438), which are due by May 1996. It appears that EPA will
             integrate new regulatory options for the metal finishing industry
             into this new guideline.  Under the anticipated scenario, effluent
             guidelines for electroplaters and metal finishers would most likely
             reference appropriate  sections of the guideline for  the metal
             products and machinery industry.  In is unclear, however, how "job
             shop"  operations, which are not part of the metal products and
             machinery industry, would be covered under this scenario.

             For Phase I of the regulation, EPA will propose effluent limitation
             guidelines for facilities  that generate wastewater while  processing
             metal  parts,   metal   products,  and machinery,  including:
             manufacture, assembly, rebuilding, repair, and maintenance.  The
             Phase I regulation  will cover seven major industrial  groups,
             including:   aircraft,  aerospace, hardware (including machine tools,
             screw machines,  metal  forgings and  stampings, metal  springs,
September 1995
97
SIC Code 34

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Fabricated Metal Products
Sector Notebook Project
            heating equipment, and  fabricated structural metal, ordinance,
            stationary industrial equipment (including electrical equipment),
            mobile industrial equipment, and electronic equipment (including
            communication equipment).  The legal deadline is May 1996.

            Phase  II, EPA  will propose effluent limitation guidelines  for
            facilities that  generate wastewater while processing metal parts,
            metal products and machinery, including:  manufacture, assembly,
            rebuilding, repair, and maintenance.  The Phase II regulation will
            cover eight major industrial groups, including:   motor vehicles,
            buses  and  trucks, household equipment, business  equipment,
            instruments, precious and nonprecious metals, shipbuilding, and
            railroads.  The legal deadline is December 31, 1997.
Clean Air Act
            In addition to the CAA requirements discussed above,  EPA is
            currently working on several regulations that will directly affect the
            metal finishing industry.  Many proposed standards will limit the
            air emissions from various industries by proposing Maximum
            Achievable Control Technology  (MACT) based  performance
            standards  that  will  set  limits  on emissions  based upon
            concentrations in the waste stream.  Various potential standards are
            described below.

Organic  Solvent  Decreasing/Cleaning

            EPA proposed a NESHAP (58 PR 62566, November 19, 1993) for the
            source category of halogenated solvent degreasing/ cleaning that
            will directly affect the metal finishing industry.  This will apply to
            new and existing  organic halogenated  solvent  emissions  to  a
            MACT-equivalent level, and will apply to new and existing organic
            halogenated solvent cleaners (degreasers) using any of the HAPs
            listed in the CAA Amendments. EPA is specifically targeting vapor
            degreasers  that  use the following HAPs:  methylene chloride,
            perchloroethylene,  trichloroethylene, 1,1,1-trichloroethane, carbon
            tetrachloride, and chloroform.

            This NESHAP proposes to implement a MACT-based equipment
            and work practice compliance standard.  This would require that a
            facility use a designated type  of pollution prevention technology
            along with proper  operating procedures.  However, EPA has also
            provided  an alternative compliance standard. Existing operations,
            which utilize performance-based standards, can continue to do so if
            such standards can be shown to achieve the same emission limit as
            the equipment and  work practice compliance standard.
 SIC Code 34
                                       98
       September 1995

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 Pa\>T\cated Metal Products
                                                           Sector Notebook Project
 Steel Picklinv. HCl
             Hydrochloric acid (HCl) and  chlorine are among the pollutants
             listed as hazardous air pollutants in Section 112 of the Clean Air Act
             Amendments of  1990.   Steel  pickling processes that use HCl
             solution and HCl regeneration processes have been identified by the
             EPA as potentially significant sources of HCl and chlorine  air
             emissions  and,  as such, a  source category  for  which  national
             emission  standards  may be  warranted.   EPA  is  required  to
             promulgate national emission standards for 50 percent of the source
             categories listed in Section 112(e) by November 15, 1997.
 Other Future Regulatory Actions
             EPA  is  developing MACT  standards  for several  industries,
             including:   miscellaneous metal parts and products (surface
             coating), asphalt/coal tar application-metal pipes, metal can (surface
             coating), metal coil (surface coating), and metal furniture (surface
             coating). The legal deadline for these rulemakings is November 15,
             2000.
September 1995
99
                                                                  SIC Code 34

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Fabricated Metal Products
                                                         Sector Notebook Project
VII.  COMPLIANCE AND ENFORCEMENT PROFILE

Background

            To date, EPA has focused much of its attention  on measuring
            compliance with specific environmental statutes.  This approach
            allows the Agency to track compliance with the Clean Air Act, the
            Resource Conservation and Recovery Act, the Clean Water Act, and
            other environmental statutes.  Within the last several years, the
            Agency has  begun to  supplement single-media  compliance
            indicators  with facility-specific,  multimedia  indicators  of
            compliance.  In doing so, EPA  is in a better position  to  track
            compliance with all statutes at the facility level, and within specific
            industrial sectors.

            A major step in building the capacity to compile multimedia data
            for industrial sectors was the creation of EPA's Integrated Data  for
            Enforcement  Analysis (IDEA) system.  IDEA has the capacity to
            "read into"  the Agency's single-media databases, extract compliance
            records, and match  the records to individual facilities.  The  IDEA
            system can match Air,  Water, Waste, Toxics/Pesticides/EPCRA,
            TRI, and Enforcement Docket records for a  given  facility, and
            generate  a list of historical permit, inspection, and  enforcement
            activity. IDEA also has the capability to analyze data by geographic
            area and corporate holder.  As the capacity to generate multimedia
            compliance data improves, EPA will make available more in-depth
            compliance and enforcement information.   Additionally, sector-
            specific measures of success for  compliance assistance efforts  are
            under  development.

 Compliance and Enforcement Profile Description

             Using  inspection, violation, and enforcement data from the  IDEA
             system, this  section provides information regarding  the historical
             compliance and enforcement activity of this sector.   In order to
             mirror the facility universe reported in the Toxic Chemical Profile,
             the data reported within this section consists of records only from
             the TRI reporting universe.  With this decision,  the  selection
             criteria are consistent across sectors with certain exceptions. For the
             sectors that do not normally report to the TRI program, data have
             been provided from EPA's Facility Indexing System (FINDS)  which
             tracks facilities in all media databases.  Please note, in this section,
             EPA does  not attempt to define the  actual number of facilities that
             fall within each sector. Instead, the section portrays the records of a
             subset of facilities  within the sector that are well defined within
             EPA databases.
  SIC Code 34
                                       100
September 1995

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 Fabricated Metal Products
                                                           Sector Notebook Project
             As  a check on the relative size of the full sector universe, most
             notebooks contain an  estimated number of  facilities  within the
             sector according to  the Bureau of Census (See Section II).  With
             sectors dominated by small businesses, such as metal finishers  and
             printers, the reporting universe within the EPA databases may be
             small in comparison to Census data. However, the group selected
             for  inclusion in this data analysis section should be consistent with
             this sector's general make-up.

             Following this introduction is  a list defining each  data column
             presented  within  this  section.    These  values  represent  a
             retrospective summary of inspections and enforcement actions,  and
             solely reflect EPA, State, and  local compliance assurance activities
             that have been entered into EPA databases. To  identify any changes
             in trends,  the EPA  ran two  data queries, one for the past  five
             calendar years (August 10, 1990 to August 9, 1995) and the other for
             the  most recent twelve-month  period (August 10, 1994 to August 9,
             1995).  The five-year analysis  gives an average level of activity for
             that period for comparison to the more recent activity.

             Because most inspections focus  on single-media requirements,  the
             data queries presented in this section are taken from  single media
             databases.  These  databases do not  provide data  on whether
             inspections are State/local or EPA-led. However, the table breaking
             down the  universe  of violations does give  the  reader a crude
             measurement of the EPA's  and States' efforts  within each media
             program.  The presented data illustrate the variations across regions
             for certain sectors.2  This variation may be attributable to State/local
             data entry variations, specific  geographic concentrations,  proximity
             to population centers, sensitive ecosystems, highly toxic  chemicals
             used in  production, or historical  noncompliance.  Hence,  the
             exhibited data do not rank regional performance or necessarily
             reflect which regions may have the most compliance problems.
2  EPA Regions include the following States: I (CT, MA, ME, RI, NH, VT); II (NJ, NY, PR, VI);
m (DC, DE, MD, PA, VA, WV); IV (AL, FL, GA, KY, MS, NC, SC, TO); V (IL, IN, MI, MN, OH,
WI); VI (AR, LA, NM, OK, TX); VII (IA, KS, MO, ME); VHI (CO, MT, ND, SD, UT, WY); IX (AZ,
CA, HI, NV, Pacific Trust Territories); X (AK, ID, OR, WA).
September 1995
101
SIC Code 34

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Fabricated Metal Products
Sector Notebook Project
Compliance and Enforcement Data Definitions

General Definitions

            Facilities Indexing System (FINDS) — this system assigns a common
            facility number to EPA single-media permit records.  The FINDS
            identification number allows EPA to compile and review all permit,
            compliance, enforcement, and pollutant release data for any given
            regulated facility.

            Integrated  Data for Enforcement  Analysis  (IDEA) — is a data
            integration  system that can retrieve information from the major
            EPA program office databases.  IDEA uses the FINDS identification
            number  to  "glue together" separate data  records from EPA's
            databases.  This is done to  create a "master list" of data records for
            any given facility.   Some  of the data systems accessible through
            IDEA are: AIRS (Air Facility Indexing and Retrieval System, Office
            of Air and  Radiation), PCS (Permit  Compliance  System, Office of
            Water), RCRIS (Resource Conservation and Recovery  Information
            System, Office of Solid Waste), NCDB (National  Compliance Data
            Base, Office  of Prevention,  Pesticides, and  Toxic Substances),
            CERCLIS  (Comprehensive   Environmental   and  Liability
            Information  System,  Superfund), and TRIS  (Toxic  Release
            Inventory System).  IDEA also contains information from outside
            sources such as Dun and Bradstreet and the Occupational Safety and
            Health Administration (OSHA). Most  data queries displayed in
            notebook Sections IV and VH were conducted using IDEA.

 Data Table Column  Heading Definitions

            Facilities in  Search ~ are based on the universe of TRI reporters
            within the listed SIC code  range. For industries not covered under
            TRI reporting requirements, the notebook uses the FINDS universe
            for executing data queries.  The SIC code range selected for each
            search is defined by each notebook's selected SlC code  coverage
            described in Section II.

            Facilities Inspected — indicates the level of EPA and State agency
             facility inspections for the facilities in this data search.  These values
             show what percentage of the facility universe is inspected in a 12 or
             60 month period.   This column does not count non-inspectional
             compliance  activities such  as the  review  of  facility-reported
             discharge reports.
 SIC Code 34
                                       102
       September 1995

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 Fabricated Metal Products
                                                          Sector Notebook Project
             Number of Inspections — measures the total number of inspections
             conducted in this sector. An inspection event is counted each time
             it is entered into a single media database.

             Average Time Between Inspections — provides an average length of
             time, expressed in months, that a compliance inspection occurs at a
             facility within the defined universe.

             Facilities with One or More Enforcement Actions - expresses the
             number of facilities  that were party to  at  least one enforcement
             action within the defined time period.  This category is broken
             down further into Federal and State actions.  Data are obtained for
             administrative, civil/judicial, and  criminal enforcement actions.
             Administrative actions  include  Notices  of  Violation (NOVs).  A
             facility with multiple enforcement actions is only counted once in
             this column (facility  with 3  enforcement  actions counts as 1).  All
             percentages that appear are referenced to the number of facilities
             inspected.

             Total  Enforcement  Actions — describes the total  number  of
             enforcement actions  identified for an industrial sector  across all
             environmental statutes.  A facility  with  multiple enforcement
             actions is  counted multiple times (a facility with  3 enforcement
             actions counts as 3).

             State  Lead Actions — shows what percentage  of  the  total
             enforcement actions  are taken by State  and local  environmental
             agencies.  Varying levels of use by States  of EPA data systems may
             limit the volume  of  actions accorded State enforcement activity.
             Some States extensively report enforcement activities into EPA data
             systems, while other States may use their own data systems.

             Federal Lead  Actions  -- shows what  percentage of the total
             enforcement actions are taken by the U.S.  EPA. This value includes
            .referrals from State agencies.  Many  of  these actions result from
             coordinated or joint State/Federal efforts.

             Enforcement to Inspection Rate — expresses how often enforcement
             actions result from inspections. This value is a ratio of enforcement
             actions to inspections, and is presented for  comparative purposes
             only. This measure is a rough indicator of the relationship between
             inspections and enforcement.   This  measure  simply  indicates
            historically how many enforcement actions can be attributed to
            inspection  activity.  Related inspections  and enforcement actions
            under  the Clean Water Act (PCS), the  Clean  Air Act (AFS) and the
            Resource Conservation  and Recovery  Act (RCRA) are included in
September 1995
103
SIC Code 34

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Fabricated Metal Products
Sector Notebook Project
            this ratio.  Inspections and actions from the TSCA/FIFRA/EPCRA
            database are not factored into this ratio because most of the actions
            taken under these programs are not the result of facility inspections.
            This ratio  does not account for enforcement actions arising from
            non-inspection compliance monitoring activities  (e.g., self-reported
            water discharges) that can result in enforcement action within the
            CAA, CWA and RCRA.

            Facilities with One or More Violations  Identified - indicates the
            number  and percentage of inspected facilities having  a violation
            identified in one of the following data categories:  In Violation or
            Significant Violation  Status (CAA); Reportable Noncompliance,
            Current  Year Noncompliance,  Significant Noncompliance  (CWA);
            Noncompliance and  Significant Noncompliance (FIFRA,  TSCA,
            and EPCRA); Unresolved Violation and  Unresolved High  Priority
            Violation (RCRA). The values presented  for this column reflect the
            extent of noncompliance within the measured time frame, but do
            not  distinguish between the severity  of the noncompliance.
            Percentages  within this column can exceed 100 percent because
            facilities can be  in  violation status without  being inspected.
            Violation status may  be a precursor to an enforcement action, but
            does not necessarily indicate that an enforcement action will occur.

            Media Breakdown of Enforcement Actions and Inspections - four
            columns  identify the  proportion  of total   inspections   and
            enforcement actions  within EPA Air,  Water,  Waste,   and
            TSCA/FIFRA/EPCRA databases.  Each column is  a percentage of
            either the  "Total Inspections," or the "Total Actions" column.


 VILA.      Fabricated Metal Products Industry Compliance History

            Exhibit  34  presents  enforcement  and  compliance  information
            specific  to the fabricated metal products industry.  As indicated in
            this exhibit, Regions  IV,  V, and IX conduct  the largest number of
            inspections in this industry. This is consistent with the fact that the
            fabricated metal products industry  is geographically concentrated
            near industrial areas.  The  data also indicates that nearly all of
            Region IV's enforcement actions are State-lead.


 VII.B.       Comparison of Enforcement Activity Between Selected Industries

             Exhibits 35 - 38 provide enforcement and compliance  information
             for selected  industries.  The  fabricated metal products industry
             comprises the largest number of facilities tracked by EPA across the
 SIC Code 34
                                       104
       September 1995

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 Fabricated Metal Products
                                                           Sector Notebook Project
             selected industries.   Likewise, it has  the largest number  of
             inspections and enforcement actions.  For this industry, RCRA
             inspections comprise over half of all inspections conducted, while
             CWA inspections account for 15 percent of  these inspections.  The
             low CWA  inspection rate is  in conflict with the large number  of
             water discharges that are generated by this industry.
September 1995
105
                            SIC Code 34

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Fabricated Metal Products
                                      Sector Notebook Project
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                                           106
                                              September 1995

-------
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                                                                      Sector Notebook Project
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                              107
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-------
Fabricated Metal Products
                                                          Sector Notebook Project
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                                     108
                                                      September 1995

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                                                                   Sector Notebook Project
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                                              Sector Notebook Project
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 Fabricated Metal Products
                                                          Sector Notebook Project
 VII.C.       Review of Major Legal Actions

 VII.C.l      Review of Major Cases

             This section provides summary information about major cases that
             have affected this sector.   As indicated in EPA's Enforcement
             Accomplishments Report, FY 1991, FY 1992, FY 1993 publications, 15
             significant enforcement actions were resolved  between 1991 and
             1993 for the metal finishing industry.  CWA violations comprised
             eight of these actions, the most of any statute. Following CWA
             violations were five  actions  involving RCRA violations,  three
             involving CERCLA violations,  one with a CAA violation,  and one
             with a  SDWA violation.  The  companies against which the  cases
             were brought are primarily metal finishers, including those that
             provide electroplating, coating, and plating services.   Two of the
             companies perform metal forming and fabrication functions.

             Twelve of the fifteen cases resulted in the assessment of a  penalty.
             Penalties  ranged from  $15,000, to  $500,000, and in  four cases,
             additional money  was spent  by the defendant to improve the
             processes or technologies and  to increase future compliance.  For
             example,  in U.S. v.  North  American Philips  Corp.  (1992). the
             company paid a $500,000 penalty and spent approximately $583,000
             to eliminate wastewater discharges from some of its non-federally
             regulated processes.    The  average  penalty per  case  was
             approximately $322,000.   Supplemental Environmental  Projects
             (SEPs) were required in two of the cases.  Texas Instruments, Inc.
             (1993), for example, was required to pay a penalty and replace a
             vapor degreaser unit with a more environmentally-protective unit.

            Although many cases involved civil penalties, four of the cases
            involved  criminal convictions, resulting in  penalties and/or jail
            sentences  for the owners and/or  operators  of the facilities.   For
            example, the case of U.S. v. Tohn Borowski and Borjohn  Optical
            Technology.  Inc..  resulted  in the first criminal  endangerment
            conviction under CWA; the company president was sentenced to 26
            months  in prison, folloshwed by two years of supervised release.
September 1995
111
                            SIC Code 34

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Fabricated Metal Products
Sector Notebook Project
VII.C.2      Supplemental Environmental Projects

            Supplementary Environmental  Projects  (SEPs) are compliance
            agreements that reduce a facility's stipulated penalty in return for
            an environmental project that exceeds the value of the reduction.
            Often, these projects fund pollution prevention  activities that can
            significantly reduce the future pollutant loadings of a facility.

            In December,  1993, the Regions were asked by EPA's Office  of
            Enforcement and Compliance Assurance to provide information on
            the number and type of SEPs entered into by  the Regions.  The
            following exhibit contains a representative sample of the Regional
            responses addressing the fabricated metal products industry.  The
            information contained in the exhibit is  not comprehensive and
            provides only a sample of the  types of  SEPs developed for the
            fabricated metal products industry.   Please note that the projects
            describes in this section do not necessarily apply to all facilities in
            this sector.  Facility-specific conditions must be considered carefully,
            when evaluating potential supplemental environmental projects.
 SIC Code 34
                                       112
       September 1995

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        Fabricated Metal Products
                                                                      Sector Notebook Project
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SIC Code 34

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Fabricated Metal Products
Sector Notebook Project

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                                              114
        September 1995

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                                                                     Sector Notebook Project
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Fabricated Metal Products
Sector Notebook Project
vni.  COMPLIANCE ACTIVITIES AND INITIATIVES

            This section highlights the activities undertaken by this industry
            sector and  public agencies to voluntarily  improve the sector's
            environmental  performance.   These  activities  include  those
            •independently initiated by industrial trade  associations.  In this
            section, the notebook  also contains a listing and  description of
            national and regional trade associations.


VIH.A.     Sector-Related Environmental Programs and  Activities

            Numerous  compliance activities  and  initiatives  are occurring
            throughout the  fabricated  metal  products  industry.   Many
            companies  are  conducting private research on developing new
            alloys and experimenting with the use of citric acid oils or terpenes
            instead of the more toxic degreasers (e.g., 1,1,1-trichloroethane).

            Several projects currently underway are sponsored by Federal, State,
            and  county  governments; universities; and trade associations.
            Several of these initiatives are described below.

Common  Sense Initiative

            The Common Sense Initiative (CSI), a partnership  between EPA
            and  private  industry, aims  to  create  environmental protection
            strategies that  are cleaner for the  environment and  cheaper for
            industry and taxpayers.   As part  of CSI,  representatives from
            Federal, State, and local governments; industry; community-based
            and  national environmental  organizations;  environmental justice
            groups; and labor organizations, come together to examine the full
            range of environmental requirements affecting the following six
            selected  industries:   automobile manufacturing; computers and
            electronics, iron and steel, metal finishing, petroleum refining; and
            printing.

             CSI participants are looking for solutions that:

             •     Focus on the industry as a whole rather than one pollutant

             •     Seek consensus-based solutions

             •     Focus on pollution prevention  rather than  end-of-pipe
                   controls

             •     Are  industry-specific.
 SIC Code 34
                                       116
       September 1995

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 Fabricated Metal Products
                                                          Sector Notebook Project
             The  Common Sense  Initiative Council  (CSIC), chaired by EPA
             Administrator  Browner,  consists of  a  parent council and six
             subcommittees  (one per  industry sector).    Each  of  the
             subcommittees have met and  identified issues and project areas for
             emphasis, and workgroups have been established to analyze  and
             make recommendation on these issues. (Contact: Greg Waldrip at
             (202)564-7024)
 Design for the Environment (DfE)
             DfE is an  EPA program  operated by  the Office of Pollution
             Prevention and Toxics. DfE is a voluntary program which promotes
             the use of safer chemicals, processes, and technologies in the earliest
             product design stages. The DfE program assists industry in making
             informed, environmentally responsible design choices by providing
             standardized analytical tools for industry application and providing
             information on the comparative environmental and human health
             risk,  cost,  and  performance  of  chemicals,  processes,  and
             technologies.  DfE  also helps  small businesses  by  analyzing
             pollution prevention  alternatives  and  disseminating   the
             information to industry and the public.  By helping  to translate
             pollution prevention into meaningful  terms, DfE contributes to
             building  the  institutional structure in corporations  to support
             pollution  prevention. DfE activities fall into  two broad categories:
             (1) the industry-specific projects which encourage businesses to
             incorporate pollution prevention into their designs; and (2) long-
             term projects that translate pollution prevention into terms  that
             make sense to professions such as chemistry,  chemical engineering,
             marketing, accounting, and insurance.

             One DfE  effort (in partnership with the Manufacturing Extension
             Partnership) is the development of a benchmarking database  and
             accompanying questionnaire to serve as an  incentive  mechanism
             for companies.  Metal fabricators are encouraged to  complete a
            company-specific  questionnaire and return it  to the Manufacturing
            Extension Partnership for.analysis.  The company will then receive
            a report comparing its data to that of other companies. Based on the
            results, companies  are  encouraged to  voluntarily  implement
            mechanisms that will minimize environmental damage resulting
            from the  manufacturing processes.  Subjects  included  in  the
            questionnaire, database, and report  range  from  the  use of
            automation and monitoring technologies to the  volumes of wastes
            generated, treated, and recycled.
September 1995
117
SIC Code 34

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r
            Fabricated Metal Products
Sector Notebook Project
            Minnesota Technical Assistance Program (MnTAP)

                        In the State of Minnesota, waste reduction is  receiving increased
                        attention as an alternative to waste disposal.  To help companies
                        reduce waste, Minnesota developed MnTAP, a program that helps
                        facilities identify waste reduction opportunities. MnTAP recognizes
                        that each company's operations are  unique and has, therefore,
                        developed a series of checklists to help identify waste reduction
                        possibilities.  The checklists are designed to assist each facility
                        evaluate wastestreams and identify waste reduction opportunities.
                        The checklists cover several areas relevant to this profile, including
                        operating procedures, cleaning, machining, plating/metal finishing,
                        coating/painting, and formulating.

                        To ensure effective use of MnTAP's checklists, staff is available to
                        answer questions over the phone  or  on-site once checklists have
                        been completed.  MnTAP has also  gathered vendor and technical
                        information for many of the options listed which may be useful in
                        assessing a facility's waste reduction opportunities.  In addition,
                        MnTAP  has developed lists of vendors  who provide recycling
                        services on a contract basis if it is not feasible  to  implement the
                        options listed on the checklists. MnTAP staff can be reached at (612)
                        625-4949.

             Pollution Prevention  and  Waste Minimization in the  Metal  Finishing Industry
             Workshop

                         The University  of Nebraska-Lincoln  sponsored  a Pollution
                         Prevention  and  Waste  Minimization in  the Metal Finishing
                         Industry workshop in  1993.  The workshop was designed for
                         managers  and  operators  of electroplating  and  galvanizing
                         operations;  engineers;  environmental  consultants;   waste
                         management consultants;  Federal, State,  and  local government
                         officials; and individuals responsible for training in the area of
                         metal finishing waste management. Topics covered included:

                         •     Saving money and reducing risk through pollution
                               prevention and waste minimization

                         •     Incorporating pollution prevention into planning
                               electroplating and  galvanizing operations

                         •     Conducting waste minimization audits

                         •     Developing and analyzing options for pollution
                               prevention/waste minimization
              SIC Code 34
                                                   118
       September 1995

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 Fabricated. Metal Products
                                                          Sector Notebook Project
             •     Innovative techniques for implementing a pollution
                   prevention/waste minimization program.

             For more information concerning this  workshop,  contact David
             Montage of the  University of Nebraska at W348 Nebraska  Hall
             Lincoln, NE 68588-0531.

 Pollution Prevention Opportunities  Checklists

             The County Sanitation Districts of Los Angeles County developed a
             detailed  pollution  prevention opportunities  checklist  to  help
             companies identify  and implement pollution prevention methods
             where  possible.   The County Sanitation Districts  has identified
             specific opportunities for the metal fabricators and metal finishing
             industries.

 Southeast Michigan  Initiative  (SEMI)

             EPA and the Michigan Department of Natural Resources (MDNR)
             have launched a geographic initiative in the Southeast Michigan
             area because of the magnitude of contaminant releases and human
             population in the area.  Eight counties within the Initiative  have
             been identified as having major environmental problems.  Several
             rivers  in the area suffer from impaired uses, polluted airsheds,
             combined sewer overflows,  contaminated  sediments,  and major
             toxic pollutant releases.

             A Steering Committee, composed of senior managers of MDNR and
             EPA, meet  quarterly  and are responsible for  making decisions
             concerning the overall direction of the Initiative.  There are also
             four working committees, including: public participation; remedial
             action  plans/sediments; pollution prevention; and compliance and
             enforcement.

            For more information regarding SEMI contact Rufus  Anderson,
            Assistant Deputy Director, MDNR Region 5  at (313) 953-1444 or
            Mardi Klevs, EPA SEMI Coordinator at (312) 353-5490.

The Blackstone Project

            The  Blackstone Project, a joint initiative by the Massachusetts
            Department of  Environmental  Protection  (DEP)   and  the
            Department of  Environmental Management (DEM), is intended to
            make environmental protection more efficient and  less costly to
            companies.   As  Doug Fine, the Compliance and Enforcement
            Coordinator, explains, the Blackstone Project's  two goals are to
September 1995
119
                            SIC Code 34

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Fabricated Metal Products
Sector Notebook Project
            encourage industry to use less toxic material in manufacturing, and
            to increase  the  efficiency of  DEP's  industrial inspections by
            conducting one-stop, facility-wide inspections.  The project focused
            first on fabricated metal products facilities near the Blackstone River
            Valley and  later expanded to all types of manufacturers in that
            region.  The State of Massachusetts now conducts facility-wide
            inspections in a continuous effort to reduce pollution.

The  NCMS/NAMF Pollution Control Assessment Project

            The National Center for Manufacturing Sciences  (NCMS) and the
            National Association of Metal Finishers (NAMF) worked jointly to
            develop the Pollution  Prevention  and   Control  Technology for
            Plating  Operations  publication  which  documents  pollution
            prevention  techniques and pollution control equipment used in
            plating operations.  To develop this document and the associated
            database,  NCMS  and  NAMF collected pollution  prevention
            information through surveys, literature  searches, and  interviews
            with industry experts.   The  resulting publication  illustrates
            pollution prevention techniques and equipment used, assesses the
            effectiveness of these techniques as illustrated by historical data, and
            indicates the types of facilities in which these  techniques  were
            employed.

The Sustainable Industry Project

            The EPA Office of Policy, Planning, and Evaluation's Sustainable
            Industry Project represents a new approach to the development of
            environmental policy for industry.   The primary goal of the
            Sustainable Industry Project is to develop, test, and  implement
            industry-specific policy recommendations that will remove barriers
             to innovation and promote strategic  environmental protection in
             the selected industries (i.e., photoimaging, metal finishing, and
             thermoset   plastics).   To  do this,  EPA  gained  a  thorough
             understanding of the relevant characteristics of the industries—the
             industry-specific  economic, institutional, cultural, technical, life-
             cycle,  and  regulatory  factors that may promote  or hinder
             environmental improvements.  Further, EPA identified driving
             factors and barriers that influence corporate decision-making and
             environmental performance.   Understanding  the factors that
             influence environmental performance in  a given  industry provides
             the basis for designing policies that will encourage improved
             performance.  Working with  industries, States, non-government
             organizations (NGOs), and other interested parties, EPA intends to
             design  policies that will protect the  environment  and human
             health while fostering competitive and sustainable industries.
 SIC Code 34
                                       120
       September 1995

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 Fabricated Metal Products
                                                          Sector Notebook Project
 U.S. Bureau of Mines (USBM)
             The U.S. Bureau of Mines has developed a technique to regenerate
             chromium  bearing solutions such as those  used  in  chromate
             conversion  aluminum electroplating. The process is in commercial
             use and  a  company is  preparing to license the technology to
             manufacture and market solution treatment equipment.  In related
             work, the Bureau worked with the specialty steel industry to reduce
             waste generated by pickling operations.   Other  USBM research
             includes the dewatering of sludges, extraction of metals from a
             variety of  liquid  and solid wastes, recycling  of metals, and
             development of lead-free free-machining copper alloys.
Wastewater Technology  Center
            The Wastewater Technology Center (WTC) is an organization of
            scientists, chemists, technologists, and support staff dedicated to the
            research and development of technologies to control industrial and
            municipal discharges.  Conducting bench-scale, pilot plant, and full-
            scale studies for 25 years, over 100 WTC staff have assisted industry
            in solving a wide variety of environmental concerns.  Recently,
            WTC has worked closely with the  Metal Finishing Task Force, a
            committee of Federal government, provincial government,  and
            metal  finishing industry representatives to  develop  a pollution
            prevention  guide.  The document is designed  to  assist metal
            finishers in establishing a pollution prevention planning process.
            WTC also provides assistance in interpreting and using this guide
            and facilitates other pollution  prevention planning programs  that
            metal finishers have or are anticipating  establishing. In addition, to
            help metal finishers  better understand and  use the  pollution
            prevention planning, WTC, in conjunction with Sheridan College,
            has prepared an extensive training course in pollution prevention
            planning in metal finishing.
September 1995
121
SIC Code 34

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Fabricated Metal Products
                                             Sector Notebook Project
Other Initiatives
            The metal finishers and platers industry is being considered by EPA
            for several upcoming initiatives. Work has already begun by the
            NPDES and  the RCRA programs.  The NPDES  Branch began an
            Industrial User initiative in May 1993 that targeted metal finishers
            who  failed to report their compliance status  with  categorical
            pretreatment effluent  standards (40  CFR 433).  In addition, the
            RCRA program has  an initiative that applies to iron and steel and
            metal plating/finishing industries.  The State of Utah plans to
            inspect each of the iron  and  steel  and metal  plating/finishing
            industries in the State.
VIII.B.
EPA Voluntary Programs
33/50 Program
            The "33/50 Program"  is EPA's voluntary program to reduce toxic
            chemical releases and transfers of 17 chemicals from manufacturing
            facilities.  Participating companies pledge to reduce their toxic
            chemical releases and  transfers by 33 percent as of 1992 and by 50
            percent as  of  1995 from the 1988 baseline year.   Certificates of
            Appreciation have been given to participants who meet their 1992
            goals. The list of chemicals includes 17 high-use chemicals reported
            in the Toxics Release Inventory.

            The number of companies that use 33/50  chemicals per industry
            sector ranged from a low of six in the tobacco industry to a high of
            1,803 in the fabricated  metal products industry. Of these companies,
            187 participate in the 33/50 program.  Some 33/50 chemicals that are
            particularly relevant  to this industry include:   lead  and lead
            compounds, methyl ethyl ketone, nickel and  nickel compounds,
            tetrachloroethylene, toluene,  trichloroethane, trichlorethylene, and
            xylenes.

            Exhibit 40 lists those companies participating in the 33/50 program
            that reported under SIC code 34 to TRI.  Many of the participating
            companies listed multiple SIC codes (in no particular order), and are
            therefore likely to conduct operations in addition to  Fabricated
            Metal Products industry.  The table shows the number of facilities
            within each company that are participating in the 33/50 program;
             each company's total 1993 releases and transfers of 33/50  chemicals;
             and the percent reduction in these chemicals since 1988.
 SIC Code 34
                                       122
                                                    September 1995

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 Fabricated Metal Products
                                                                   Sector Notebook Protect
                                       Exhibit 40
                                    33/50 Program

A B Chance Co.
ABC Holdings Inc.
Acme Metals Inc.
Adolph Coors Company
Aero Metal Finishing Inc.
Akzo Nobel Inc.
Aladdin Industries Inc.
All Metal Stamping Inc.
Allied-Signal Inc.
Aluminum Company Of America
America's Best Quality
American National Can Company
Ameron Inc. Delaware
Amsted Industries Incorporated
Anderson Screw Products Inc.
Anomatic Corporation
Apogee Enterprises Inc.
Armco Inc.
Asea Brown Boveri Inc.
Asko Processing Inc.
Atlas Die Inc.
Atlas Plating Inc.
Automatic Pltg Of Bridgeport
B. L. Downey Co. Inc.
Baker Hughes Incorporated
Ball And Socket Mfg. Co. Inc.
Ball Corporation
Bausch & Lomb Incorporated
Bead Industries Inc.
Bethlehem Steel Corporation
BHP Holdings (USA) Inc.

Centralia
Eufaula
Riverdale
Golden
Fenton
Chicago
Nashville
Abbotsford
Morristown
Pittsburgh
Milwaukee
Chicago
Pasadena
Chicago
Jamestown
Newark
Minneapolis
Pittsburgh
Stamford
Seattle
Elkhart
Cleveland
Bridgeport
Broadview
Houston
Cheshire
Muncie
Rochester
Bridgeport
ethlehem
an Francisco

MO
AL
IL
CO
MO
IL
TN
WI
NJ
PA
WI
IL
CA
L
NY
OH
MN
PA
CT
WA
N
OH
CT
L
TX
CT
N
NY
CT
A
A
SIC Codes
3644, 3613, 342
2851, 344
3312,3499,3479
339
2082,3411,344
347
341
3086, 3469, 364
3429, 3469, 3499
3728, 3471, 3724
3463
3471
3411
3272, 3317, 3443,
3479
3315, 3496, 3471
3451
3471
3479
3446
3443
3479
3479
3471
3471
3479
3533, 3471
3965, 3469, 3471
3411
3471,3851,3827
3499, 3679, 3432
3312,3462
3479
#ofParticipafin
Facilities
1
4
5
1
1
1
1
1
2
5
1
9
1
1
1
1
1
2
2
2
1
1
1
1
1
1
7
1
1
1
1
1993 Release
and Transfer
(Ibs.)
59,90
55,23
157,23
158,79
12,90
930,18
53,74
1,112
2,080,50
2,403,017
1,025
2,303,898
184,882
1,834,493
7,860
403,270
423,862
1,849,709
501,017
36,991
26,400
505
635
250
193,116
9,820
721,859
51,706
107,143
792,550
64,365
% Reduction
1988 to 1993
***
**
38
59
43
13
91
50
50
51
74
50
**
66
100
50
15
4
50
50
100
33
*** 11
75
20
**
86
*
*#*
50
***
September 1995
123
                                                                            SIC Code 34

-------
Fabricated Metal Products
Sector Notebook Project
                                 Exhibit 40 (cont'd)
                                  33/50  Program
Parent Facility name
lack & Decker Corporation
laser Die Casting Co.
me Industries Inc.
BtOd & Mcclung-Pace Co.
toofclynParkOilCo.Inc.
umham Corporation
C. A. Dahlin Co.
:ald\vdl Products Inc.
Canon Business Machines Inc.
Cargill Detroit Corporation
Channcllock Inc.
3iart Industries Inc.
Chrysler Corporation
;old Heading Co.
Collis Inc.
Commercial Enameling Co.
'onagra Inc.
Cooper Industries Inc.
Corning Inc.
"renlo Inc.
'jovm City Plating Co.
town Cork & Seal Company
Crown Metal Finishing Co. Inc.
)ana Corporation
3avis St. Hcmphill
Delbar Products Inc.
3elta Engineering & Mfg. Co.
)mton Company
)uo-Fast Corp.
Jynamlc Metal Products Company
saglc-Picher Industries Inc.
•aton Corporation
Huron Industries Inc.
Hectro-Platcrs Of York Inc.
Emerson Electric Co.
snamcicrs & Japanncre Inc.
Ernie Green Industries Inc.
Exccll Polishing & Buffing Co.
Federal-Mogul Corporation
{'eldkircher Wire Fabg Co.

altimore
cattle
Minneapolis
ortland
Minneapolis
Lancaster
Ik Grove
Village
Abilene
Costa Mesa
Clawson
Meadville
Willoughby
Highland Park
Detroit
Clinton
Huntington
Park
Omaha
Houston
Coming
Rochester
El Monte
Philadelphia
Kenilworth
Toledo
Elkridge
Perkasie
Tualatin
Danville
Franklin Park
Manchester
Cincinnati
Cleveland
Aumsville
Wrightsville
Saint Louis
Chicago
Dayton
Wadsworth
Southfield
Nashville

MD
WA
MN
OR
MN
A
L
TX
CA
MI
PA
OH
MI
MI
A
CA
NE
TX
NY
MN
CA
PA
NJ
OH
MD
PA
OR
VA
IL
CT
OH
OH
OR
PA
MO
IL
OH
OH
MI
TN

3429
3471
3479
3433, 3564, 3585
3364, 3471
3433
3469
3471
3479
3462
3423
3443
3465
3471
3496, 3471, 3499
3431
3411
3462, 3317
3469, 3471
3444
3471
2752, 3479
3479
3451, 3492
3451
3089, 3465
3444
3425
346
3444
3053, 347
346
347
347
3569, 3541, 3496
344
347
346
347
3365, 3366, 347
3471, 349
Facilities
6
1
1
1
1
1
1
1
1
1
1
2
2t
i
i
i
i
7
1
1
1
20
1
3
1
2
1
1
1
1
3
4
1
1
4
1
3
1
3
1
nd Transfers
(Ibs.)
487,188
38,900
207,147
20,300
12,606
34,149
12,900
11,880
5
717,558
118,913
8,260
3,623,717
16,021
63,010
250
39,588
1,048,465
1,521,528
66,945
151,509
1,236,689
50,282
1,652,123
13,365
102,983
8,239
27,00
652,51
25
227,24
450,21
4,35
29,46
2,140,49
40,00
329,82
13,14
255,99

1988 to 1993
50
78
5

13
96

50
95
31

/y
80
jz

100

75
14

j\j
DU
21


50













18
 SIC Code 34
                                           124
        September 1995

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 Fabricated Metal Products
                                                                  Sector Notebook Project
                                  Exhibit 40 (cont'd)
                                   33/50 Program

Fleet Design Inc.
Fmc Corporation
Ford Motor Company
Foto Mark Inc.
Fulcrum II Limited Partnership
G M Nameplate Inc.
G. W. Lisk Co. Inc.
Gates Corporation
Gayston Corporation
Gefinor (USA) Inc.
General Dynamics Corporation
General Electric Company
General Motors Corporation
Gillette Company
Globe Engineering Company Inc.
Hager Hinge Company
Halliburton Company
Hand Industries Inc.
Handy & Harman
Harrow Industries Inc.
Harsco Corporation
Henkel Corporation
Heresite Protective Coatings
Hi-Shear Industries Inc.
HM Anglo-American Ltd
Hohman Plating & Mfg. Inc.
Hoover Sys. Inc.
Houston Plating Co.
IBM
Illinois Tool Works Inc.
Imagineering Enterprises Inc.
Inco United States Inc.
Jrarcnt Oity
Portland
Chicago
Dearborn
Mendota
Heights
New York
Seattle
Clifton Springs
Denver
Springboro
New York
St Louis
Fairfleld
Detroit
Boston
Wichita
Saint Louis
Dallas
Warsaw
New York
Grand Rapids
Camp Hill
Kng Of Prussa
Manitowoc
New Hyde
Park
New York
Dayton
Dallas
South Houston
Armonk
Glenview
South Bend
New York
Si
TN
IL
MI
MN
NY
WA
NY
CO
OH
NY
MO
CT
MI
MA
KS
MO
TX
IN
NY
MI
PA
PA
WI
NY
NY
OH
TX
TX
NY
L
N
NY
SIC Codes
347
3462, 3324, 3325
3465, 371
3479
3462
2759, 2752, 3679
3993, 3471, 3479
3499, 3451, 3471
3491
3429, 3451
3483, 3463
3471, 3951
3441, 3621
3444, 3724
3651, 3694, 3679
3672, 3471
3421
3728, 3724, 3444,
3599
3429
3443
3471
3471, 3469
3429
3469, 3449
3479
3479, 2851, 2821
3452, 3471, 3451,
3479
3423
3471, 2851, 3479
2542, 3444, 3441
3471
3672, 3579, 3471
3469
3471
3462, 3463
# of Farticipatin
Facilities
3
1
5
1
1
1
1
1
1
1
1
7
15
1
1
2
1
1
3
1
8
1
1
1
4
1
1
1
1
3
1
1
1993 Releases
and Transfers
(Ibs.)
52
502,31
15,368,032
73,325
77,680
15,405
15,548
478,941
33,355
9,088
588,246
5,010,856
16,751,198
21,497
18,678
97,121
16,884
37,000
477,150
128,355
415,574
164,363
367
8,226
1,265,741
13,293
510
997
1,411,304
673,128
11,282
346,594
% Reduction
1988 to 1993
80
50
15
5
24
50
*
***
56
50
84
50
*
99
*
64
**
***
50
*
**
55
50
50
2
**
27
*
1
***
***
26
September 1995
125
SIC Code 34

-------
Fabricated Metal Products
Sector Notebook Project
                                 Exhibit 40 (cont'd)
                                  33/50 Program
1 Parent Facility name
IndiU Ltd
|tmlitnhead Plating Inc.
Industrial Hard Chrome Ltd.
IngcrsoII-Rand Company
IJIntcrlakc Corporation
(International Paper Company
JITT Corporation
luaeobson Mfg Co. Inc.
ueffcrson City Mfg. Co. Inc.
Juor-Mac Company Inc.
Jlordan-Edmiston Group Inc.
Kaspar Electroplating Corp
JKclso Asi Partners L P
JKenncdy Mfg, Co.
Kitzinger Cooperage Corp
Lacks Enterprises Inc.
Lawrence Brothers Inc.
|]LCCO Corporation
llutton Industries Inc.
IJLord Corporation
IjLonn Ind.
jjLTV Steel Co. Inc.
jJLukc Engineering & Mfg Corp
iJMacklanburg-Duncan Co.
IjMarmon Group, Inc.
[Martin Marietta Corporation
|]Masco Industries Inc.
JMascotcch
IJMatcc Corporation
IJMeaden Screw Products Company
[[Mechanical Galv-Plating Corp
IJMeco Inc.
IJMclallics Inc.
[[Metromedia Company
[(Midwest Plating Company Inc.
Parent City
Weston,
ntario,
anada
hippewa Falls
eneva
Woodcliff
ake
isle
urchase
New York
Kenilworth
efferson City
Grafton
New York
hiner
New York
Van Wert
Saint Francis
Grand Rapids
Sterling
Saint Joseph
Beverly Hills
Erie
Muskegon
Cleveland
Wadsworth
Oklahoma City
Chicago
Bethesda
Taylor
Taylor
Hopkinton
Burr Ridge
Sidney
Paris
Onalaska
E Rutherford
Grand Rapids


WI
L
NJ
L
NY
NY
NJ
MO
WI
NY
TX
NY
OH
WI
MI
IL
MI
CA
PA
MI
OH
OH
OK
IL
MD
MI
MI
MA
IL
OH
IL
WI
NJ
MI

3442
3471
3471
3429
3441
8731, 3471, 3544
3471,3479,3498
3452
3363, 3451, 3469
3499, 3479
3421
3471
3585, 3433, 3564
3469
3412, 5085, 5805
3089, 3471
3429
3826, 3471, 3229
3731, 3441, 3443
3069, 347
3471, 3354
347
347
342
345
3769, 3499, 3479
347
3398, 347
346
3479, 2899, 348
345
347
344
347
3451, 349
347
Facilities
3
1
2
4
1
1
3
1
1
1
1
1
1
^
1
3
1
1
1
2
1
1
1
1
5
1
13

1
1
1
1
1
1
1
nd Transfers
(Ibs.)
303,909
14,005
13,213
96,553
159,932
2,784,831
735,332
12
4,850
4,995
332,930
56
355,557
69,756

867,354
6,827
6,800
•^ '
1,111,309
25,500
612,924
6,60
23,37
1,092,21
223,28
488,48
3,163,83
21,80
12,86
3,44
51,86
27,72
295,32

1988 to 1993
*


60
37
50




27

43
80
50
27

14


50



1
73






jU

50
 SIC Code 34
                                            126
        September 1995

-------
 Fabricated Metal Products
                                                                  Sector Notebook Project
                                  Exhibit 40 (cont'd)
                                    33/50 Program
f aient facility Ikclille
Miller Smith Mfg. Co.
Modern Metal Products Co.
Modern Welding Company
Modine Manufacturing Company
Morgan Stanley Leveraged Fund
Napco Inc.
Nashua Corp.
National Forge Company
National Semiconductor Corp. -
New Dimension Plating Inc.
Newell Co.
Norandal USA
North American Investment Prop
Northland Stainless Inc.
Norton Company
Oak Industries Inc.
Oberg Industries Inc.
Oregon Sand Blasting & Coating
Owens-Illinois Inc.
Pace Industries Inc.
Parker Hannifin Corporation
Pechiney Corporation
Penn Engineering & Mfg
Philip Morris Companies Inc.
Photocircuits Corporation
PMF Ind. Inc.
Precision Plating Inc.
Precision Products Group Inc.
Premark International Inc.
Process Engineering Co. Inc.
Production Paint Finishers
Prospect Purchasing Co. Inc.
Parent City
Spring Lake
Loves Park
Owensboro
Racine
New York
Valencia
Nashua
Irvine
Santa Clara
Hutchinson
Freeport
Brentwood
Hawthorne
Tomahawk
Worcester
Waltham
Freeport
Tualatin
Toledo
New York
Cleveland
Greenwich
Danboro
New York
Glen Cove
Williamsport
Minneapolis
Rockford
Deerfield
ackson
Bradford
N Brunswick
SJl
MI
IL
KY
WI
NY
PA
NH
PA
CA
MN
IL
TN
NY
WI
MA
MA
PA
OR
OH
NY
OH
CT
PA
NY
NY
PA
MN
L
L
MS
OH
NJ
SIC Codes
347
347
3441, 3443
3443, 3714
3724, 347
3499, 3444, 3446
3442, 3479
2672, 3572, 3577
2869, 2821, 3479
3462
3679, 3674, 3471
3471
3471, 3496
3353, 3479
3443
3443
3425
3451, 3471, 3398
3469, 3471, 3089
3479
3469
3639, 3444, 3469
3451, 3492, 3494
3479, 3724
3452
3479, 3468
3672, 3471
3499, 3471
3471
3398, 3469, 3495,
3493, 3499
3556, 3325, 3444
3471
3479
3412
# of Participatin
Facilities
- 1
1
1
4
2
1
2
1
1
1
5
1
1
1
1
1
1
1
2
1
9
1
1
1
1
1
1
1
2
1
1
1
1993 Releases
and Transfers
(Ibs.) .
17,247
163
5
488,996
2,166,420
41,037
1,818,504
3,100
23,173
17,300
324,283
627,740
11,755
7,570
40,831
34,128
18,435
14,660
412,573
14,530
244,966
216,177
111,897
259,053
292,178
13,015
10,155
149,834
140,313
10,305
11,584
47,275
% Reduction
1988 to 1993
***
71
*
50
13
60
*#
*
6
35
23
6
70
***
63
16
85
*
#**
**
50
***
100
**
92
34
#**
***
***
50
60
50
September 1995
127
SIC Code 34

-------
Fabricated Metal Products
Sector Notebook Project
                                 Exhibit 40 (cont'd)
                                   33/50 Program
Parent Facility name
Protective Coatings Inc.
Providence Metallizing Co. Inc.
uality Rolling & Deburring Co.
R P Adams Company Inc.
Raytheon Company
Rehrig International Inc.
Reilly Plating Co.
Reliance Finishing Co.
teynolds Metals Company
S,K. Williams Co.
Schullcr Corporation
Seneca Foods Corporation
Sicbc Industries Inc.
Skills Inc.
Smith Everett Investment Co.
Smith System Manufacturing Co.
Sommcr Metalcraft Corp
Sonoco Products Company
Southline Metal Products Co.
Spx Corporation
Stanley Works
Sunset Fireplace Fixtures
Super Radiator Coils Ltd
Superior Plating Inc.
Surftcch Finishes Company
Swva Inc.
"awas Plating Company
Tech Industries Inc.
fcchmctals Inc.
Tektronix Inc.
fcnneeo Inc.
Texas Instruments Incorporated
rhcrma-Tru Corp
fhiokol Corporation
fhomas Steel Strip Corp
Trinova Corporation
J T I Corporation
United States Can Company Del
United Technologies Corp
US Can Corporation (Del)
Parent City
Kent
awtucket
Thomaston
Tonawanda
Lexington
Richmond
Nanticoke
Grand Rapids
Richmond
Wauwatosa
Denver
Pittsford
Richmond
Seattle
Milwaukee
Piano
Crawfordsville
Harts ville
Houston
Muskegon
New Britain
City Of
Industry
Minneapolis
Minneapolis
Kent
Huntington
Tawas City
Woonsocket
Dayton
Beaverton
Houston
Dallas
Sylvania
Ogden
Warren
Maumee
Collegeville
Hinsdale
Hartford
Oak Brook
SI
WA
RI
CT
NY
MA
VA
PA
MI
VA
Wl
CO
NY
VA
WA
WI
TX
N
SC
TX
MI
CT
CA
MN
MN
WA
WV
MI
RI
OH
OK
TX
TX
OH
UT
OH
OH
PA
IL
CT
IL
SIC Codes
3471,3479
3479, 3471
3471
3469
3672, 3471, 3674
3471
3471
3479
3479
3471
3444
3411
3400, 3471
3479
3444
3444, 2531
3471
2655, 3469
3412
3479
3471
3429
3400
3471
3471
3441
3471
3089, 3471
347
3663, 3444
344
3822, 2812, 3356
3471, 3714, 334
3442, 308
345
3471, 331
3451, 349
346
3412, 341
3086, 347
341
Facilities
1
1
1
1
1
1
1
1
1
1
1
1
2
1
1
1
1
2
i
i
10
1
1
1
1
1
1
1
1
1
1
1
1
2
1
1
1
1
2
7
nd Transfers
(Ibs.)
41,137
35,347
287,324
20
706,045
2,261
750
11,400
2,055,294
126
24,694
19,717
849,335
7,650
240,445
499
1,500
621,380
77,552
554,822
508,199
12,800
139,235
39,406
20,270
43,405
3,265
27,003
10,645
12,393
1,272,423
344,22
17,25
1,001,16
6,83
488,87
473,87
5,29
2,393,25
573,08
1988 to 1993

70


50

2




50
2




1

•^
50
25



27
50
64
50

8
25
41
4U


DU



 SIC Code 34
                                           128
        September 1995

-------
 T?abdicated Metal Products
                                                          Sector Notebook Project
                              Exhibit 40 (cont'd)
                               33/50 Program
iaircni c siC-ility iimii^
Valley Plating Works
Galley Technologies Inc.
Van Der Horst Usa Corporation
/eba Corporation
W W Custom Clad Inc.
W. J. Roscoe Co.
Walter Industries Inc.
Warner-Lambert Company
Weiss-Aug Co. Inc.
Wheeling-Pittsburgh Corp
Whirlpool Corporation
Whyco Chromium Company Inc.
Winona Corporation
Wisconsin Tool & Stamping Co.
WNA Inc.
Worldwide Cryogenics Holdings
Wright Products Corp
ifork Metal Finishing Co.
Zippo Manufacturing Company
Parent C^ity
Los Angeles
Valley Park
Terrell
Houston
Canajoharie
Akron
Tampa
Morris Plains
East Hanover
Wheeling
Benton Harbor
Thomaston
Winona Lake
Schiller Park
Wilmington
Minneapolis
Minneapolis
Philadelphia
Bradford
SJL
CA
MO
TX
TX
NY
OH
FL
NJ
NJ
WV
MI
CT
IN
IL
DE
MN
MN
PA
PA
SIC Codes
3471
3398, 3463
3471
3471, 3599
3471
2851,2891,2517,
3479
3321, 3479
3421
3465, 3469
3479
3450, 3471, 3490
3471
3479
3469
3449
3443
3429
3471
3421
# of Participating
Facilities
1
1
1
1
1
1
1
1
1
1
1
1
1
1
2
1
1
1
2
1993 Releases
and Transfers
(Ibs.)
130
0
20,623
24,254
8,595
40,051
859,751
146,333
15,834
560,055
1,540,866
88,737
47,260
42,000
248,148
133,810
45,287
5
189,929
% Reduction
1988 to 1993
75
#*
#*
10
50
50
***
40
**
66
50
50
50
**
*##
*
#*#
*
50
* = not quantifiable against 1988
ata.
** = use reduction goal only.
*** = no numerical goal.
Environmental  Leadership Program
            The Environmental  Leadership  Program  (ELP)  is  a national
            initiative piloted by EPA and State agencies in which facilities have
            volunteered   to  demonstrate   innovative  approaches  to
            environmental management and compliance.  EPA has selected 12
            pilot projects at industrial facilities  and Federal installations which
            will demonstrate the principles of  the  ELP program.  These
            principles  include:     environmental  management  systems,
            multimedia compliance assurance,  third-party  verification of
            compliance, public  measures  of  accountability,  community
            involvement, and mentoring programs. In return for participating,
            pilot participants receive public recognition and are given a period
            of  time to  correct  any  violations  discovered  during  these
            experimental projects.  At present, no metal finishing or fabricating
            facilities are carrying out ELP pilot projects.  (Contact:  Tai-ming
September 1995
129
SIC Code 34

-------
Fabricated Metal Products
Sector Notebook Project
Project XL
            Chang, ELP Director, (202) 564-5081 or Robert Fentress, (202) 564-
            7023)

            Gillette ELP Project

            The objective of the Gillette Environmental Leadership Program is
            the development and implementation of a third party compliance
            and management systems  audit and  verification process.  The
            project  will  involve  the  development   of  environmental
            compliance  and environmental management systems  audit
            protocol criteria  that can be adopted and easily implemented by
            other facilities to assess compliance with relevant regulations. The
            three Gillette facilities that are participating  are:  South  Boston
            Manufacturing  Center,  blade and razor manufacturing; North
            Chicago Manufacturing Center, batch chemical manufacturing; and
            Santa Monica,  CA, stationary products manufacturing.  (Contact:
            Scott Throwe, (202) 564-7013).
            Project XL was  initiated  in March  1995 as a part of President
            Clinton's Reinventing  Environmental  Regulation  initiative.   The
            projects seek to  achieve cost effective environmental benefits by
            allowing participants to  replace or  modify  existing regulatory
            requirements  on  the  condition  that they produce  greater
            environmental benefits.    EPA and program participants  will
            negotiate and sign a Final Project Agreement, detailing specific
            objectives that the regulated entity shall satisfy. In exchange, EPA
            will allow the participant  a certain degree of regulatory flexibility
            and may  seek changes  in underlying regulations or statutes.
            Participants are encouraged to seek stakeholder support from local
            governments, businesses,  and  environmental groups.  EPA hopes
            to  implement fifty  pilot  projects  in four categories including
            facilities, sectors, communities, and government agencies regulated
            by EPA. Applications will be accepted on a rolling basis and projects
            will move to implementation within six months of their selection.
            For additional  information  regarding XL  Projects,  including
            application procedures and criteria, see the May 23, 1995 Federal
            Register Notice.  Contact Jon Kessler, Office of Policy Analysis, (202)
            260-4034.
 Green Lights  Program
             EPA's Green Lights program was initiated in 1991 and has the goal
             of preventing pollution by encouraging U.S.  institutions to use
             energy-efficient lighting technologies. The program has over 1,500
 SIC Code 34
                                      130
       September 1995

-------
 fabricated Metal Products
                                                          Sector Notebook Project
             participants which include major corporations; small and medium
             sized businesses; Federal, State and local governments; non-profit
             groups; schools;  universities;  and health care  facilities.   Each
             participant is required to survey their facilities and upgrade lighting
             wherever it is profitable.  EPA provides technical assistance to the
             participants  through a  decision support software package,
             workshops and manuals,  and a financing registry.  EPA's Office of
             Air  and Radiation is responsible for  operating  the Green Lights
             Program.  (Contact:  Susan Bullard, (202) 233-9065 or  the Green
             Light/Energy Star Hotline at (202) 775-6650)
 WasteWi$e  Program
            The WasteWi$e Program was  started in 1994 by EPA's  Office of
            Solid Waste  and Emergency Response.  The program is  aimed at
            reducing municipal solid wastes by promoting waste minimization,
            recycling collection, and the  manufacturing and  purchase  of
            recycled products. As of 1994, the program had about 300 companies
            as members, including a number of major corporations.  Members
            agree to identify and implement actions to reduce their solid wastes
            and must provide EPA with their waste reduction goals along with
            yearly progress reports.  EPA in turn provides technical assistance to
            member companies and allows the use of the WasteWi$e logo for
            promotional purposes.  (Contact: Lynda Wynn, (202) 260-0700 or the
            WasteWi$e Hotline at (800) 372-9473)
Climate Wise  Recognition Program
            The Climate Change Action Plan was initiated in response to the
            U.S.  commitment  to  reduce greenhouse gas emissions  in
            accordance with the Climate Change Convention of the 1990 Earth
            Summit. As part of the Climate Change Action Plan, the Climate
            Wise Recognition Program is a partnership initiative run jointly by
            EPA and the Department of Energy.  The program is designed to
            reduce greenhouse gas emissions by encouraging reductions across
            all sectors  of the economy, encouraging participation in the  full
            range of Climate  Change Action Plan initiatives, and fostering
            innovation.  Participants in the program  are required to identify
            and commit to  actions that reduce greenhouse gas emissions.  The
            program, in turn, gives organizations early recognition for their
            reduction commitments;  provides technical assistance  through
            consulting services, workshops, and guides; and provides access to
            the program's  centralized  information  system.   At EPA,  the
            program is operated by the Air and Energy Policy Division within
            the Office of Policy Planning and Evaluation.  (Contact: Pamela
            Herman, (202) 260-4407)
September 1995
131
                            SIC Code 34

-------
Fabricated Metal Products
Sector Notebook Project
NICE3

            The U.S.  Department of Energy  and EPA's Office  of Pollution
            Prevention are jointly administering a grant program  called The
            National  Industrial  Competitiveness   through  Energy,
            Environment, and Economics (NICE3). By providing grants of up
            to 50 percent of the total project cost, the program encourages
            industry to reduce industrial waste at its source and become more
            energy-efficient  and cost-competitive through waste minimization
            efforts.  Grants are used by industry to design, test, demonstrate, and
            assess the feasibility of new processes and/or equipment with the
            potential to reduce pollution and  increase energy efficiency.  The
            program is open to all  industries; however, priority is given to
            proposals  from participants in the  pulp and  paper,  chemicals,
            primary metals,  and petroleum and coal products sectors. (Contact:
            DOE's Golden Field Office, (303) 275-4729)


VIH.C.      Trade Association/Industry Sponsored Activity

            Associations, universities, and  the industry are  currently working
            with EPA to make  the Agency aware of issues that relate to metal
            fabricating  and finishing  industries.   As a result of  these
            relationships and  overall interest in achieving compliance and
            reducing  pollution,  additional  research  relating  to  process
            techniques  and  pollution prevention  alternatives  is  being
            conducted.  Various workshops and training opportunities have
            resulted from these efforts.  A summary of some trade association
            and  industry activities is  presented below,  along with some
            associations related to this industry.

VTTT.C.l.    Environmental  Programs

            Several trade and professional associations are working with EPA to
            make the Agency aware of issues that relate to metal fabricating
            industries.  For example, the Copper and Brass Fabricators Council
            (CBFC) has  been assisting EPA's  Office of Solid Waste regarding
            recycling issues as it develops or redrafts RCRA regulations.  CBFC
            is communicating its experiences with metal fabricating to EPA, in
            terms of materials used and possible recycling options, in hopes that
            future regulations might complement the industry's processes.

            Additionally, several organizations have sponsored  workshops
            focusing on waste  minimization  and  pollution prevention in
             several fabricated metal related industries.  Three workshops,  the
 SIC Code 34
                                      132
       September 1995

-------
Fabricated Metal Products
                                                        Sector Notebook Project
            Hazardous Waste Management for Small Business Workshop, the
            Environmentally Conscious Painting  Workshop, and the Pollution
            Prevention Workshop for the Electroplating Industry, are discussed
            below.

Hazardous  Waste Management for Small Business Workshop

            The University of Northern Iowa, with support from EPA, Des
            Moines Area  Community  College,  Northeast Iowa Community
            College, Scott  Community College, and Indiana Hills Community
            College,  sponsored  a Hazardous  Waste  Management for  Small
            Business workshop.   This  workshop was geared towards  small
            businesses and  was  intended to provide practical answers to
            environmental regulatory questions.  Small businesses covered by
            the workshop  include:  manufacturers,, vehicle maintenance and
            repair  shops, printers, machine shops, and other businesses that
            generate potentially  hazardous waste.  Topics covered include:
            hazardous waste  determination, waste generator categories,
            management of specific common waste streams, including used oil
            and  solvents, and  pollution prevention.   (Contact:  Duane
            McDonald, (319) 273-6899)

Environmentally Conscious Painting  Workshop

            Kansas State  University, NIST/Mid-America  Manufacturing
            Technology Center, Kansas  Department of Health  & Environment,
            EPA Region 7, Allied Signal, Inc., Kansas City Plant, and the U.S.
            Department of Energy sponsored the Environmentally Conscious
            Painting  workshop.   This workshop covered  topics  such as
            upcoming regulations and the current regulatory climate, methods
            to  cost-effectively reduce  painting  wastes  and  emissions, and
            alternative painting processes.   (Contact:  the Kansas  State
            University Division of Continuing Education, (913) 532-5566)

Pollution Prevention Workshop for the Electroplating Industry

            Kansas State University  Engineering Extension,  EPA  Region 7,
            Kansas Department of Health  and  Environment,  and the
            University of Kansas  sponsored  the  Pollution   Prevention
            Workshop for the  Electroplating Industry.  The workshop described
            simple techniques  for waste  reduction in the  electroplating
            industry, including:   plating, rinsing processes and wastewater,
            wastewater management  options, metals recovery options, waste
            treatment and  management, and product substitutions and plating
            alternatives.  (Contact: the Kansas State  University Division of
            Continuing Education, (800) 432-8222)
September 1995
133
SIC Code 34

-------
Fabricated Metal Products
        Sector Notebook Project
VTTT.C.2.     Summary of Trade Associations

            Various trade associations represent the interests of metal fabricator
            workers and the industry itself.  Some of these organizations are
            discussed in greater detail below.
American Electroplaters and Surface Finishers
Society (AESF)
12644 Research Parkway
Orlando, FL 32826
Phone: (407)281-6441
Fax: (407)281-6446
Members:
Staff:
Budget:
Contact:


10,000
21
2,000,000
Ted Witt, Executive
Director

            Founded in 1909, AESF is an international professional society of
            scientists, technicians, job shop operators, and others interested in
            research in electroplating, surface finishing, and allied arts. AESF
            offers classroom training courses, home study courses, cooperative
            programs, and a voluntary certification program.  In addition, it
            bestows  awards, 'conducts research programs, and provides an
            insurance program  for job shop owners.  AESF  also publishes
            Plating and  Surface Finishing (monthly), AESF  Shop Guide, books,
            symposia proceedings, research reports, and training booklets with
            slide presentations; and makes available films and videotapes.
             ASM International (ASM)
             9639 Kinsman
             Materials Park, OH 44073
             Phone: (216)338-5151
Members: 54,000
Staff: 145
Budget: $19,500,000
Contact: Edward L. Langer
             Founded in  1920,  ASM  represents  metallurgists;  materials
             engineers; executives  in materials  producing and consuming
             industries; and teachers and students.  This association disseminates
             technical information about the manufacture, use, and treatment of
             engineered materials.  It offers in-plant, home  study, and intensive
             courses  through  the Materials Engineering Institute;  conducts
             conferences, seminars, and lectures; presents awards to teachers of
             materials science  and  for achievements in the field; and grants
             scholarships and fellowships.  Additionally, it maintains a library of
             10,000 volumes on metals and other materials.
 SIC Code 34
                                       134
               September 1995

-------
 Fabricated Metal Products
                                                            Sector Notebook Project
             Copper and Brass Fabricators Council (CBFC)
             1050 17th Street, NW, Suite 440
             Washington, DC 20036
             Phone: (202)833-8575	
            Contact: Joseph L. Mayer
             Founded in 1966, CBFC represents copper and brass fabricators. Its
             activities  involve foreign trade  in copper  and  brass  fabricated
             products, and Federal  regulatory  matters including legislation,
             regulations, rules, controls, stockpiling, and other  similar measures
             affecting domestic fabricators of copper and brass  products.  CBFC
             holds an annual  convention.
             Metal Construction Association (MCA)
             1101 14th Street, NW, Suite 1100
             Washington, DC 20005
             Phone: (202)371-1243
             Fax: (202)371-1090
            Members: 100
            Staff: 5
            Contact:  David W. Barrack
             Founded in  1983,  MCA represents individuals  engaged in the
             manufacture, design, engineering, sale, or installation of metal used
             in  construction, and others interested  in  the metal construction
             industry.   It promotes the  use  of metal  in  all  construction
             applications.  Additionally, MCA represents all sectors of the metal
             construction industry; fosters better trade practices and improved
             communication  within  the  industry; serves as liaison between
             members and other industry organizations.  The association collects
             and disseminates information; maintains the Merit Award Program
             to acknowledge outstanding buildings, products, and systems in the
             industry; plans  programs in institutional  advertising, voluntary
             standards, and statistics; proposed educational programs including
             structure erection, estimating, and bookkeeping; compiles statistics;
             and bestows scholarships.  MCA also prepares and distributes two
             publications:  the  Metal  Construction Association-Membership
             Directory (annually)  and  the Metal  Construction  Association-
             Newsletter (quarterly).   Its newsletter includes technical  articles,
             meeting reviews, committee reports,  minutes, and a calendar of
             events.   MCA  holds  a  semiannual  meeting and  Metalcon
             International Trade  Show and an annual meeting.
September 1995
135
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Fabricated Metal Products
                   Sector Notebook Project
            Metal Fabricating Institute (FMI)
            PO Box 1178
            Rockford,IL 61105
            Phone: (815)965-4031	
           Staff: 4
           Contact: Ronald L. Fowler
            Founded in 1968, MFI conducts technical seminars for structural
            and sheet  metal fabricators  to update management on the latest
            manufacturing  techniques.   MFI  also presents  a Fabricating
            Engineer  of the Year  Award.   In  addition,  it publishes Metal
            Fabricating News (bimonthly), which contains a calendar of events,
            new products and literature, book reviews, and  a buyers guide.  The
            association also holds a semiannual conference in West Lafayette,
            Indiana.
            Metal Finishers Suppliers Association (MFSA)
            801 North Cass, Ste. 300
            Westmont, IL 60559
            Phone: (708)887-0797	
           Members: 180 Companies
           Staff: 2-4
           Budget: $400,000
           Contact:  Richard Grain
            Incorporated  in  1951,  MFSA  is the  only  trade association
            representing companies that  supply chemicals and  equipment to
            the  metal  finishing  industry.    MFSA  works   closely  with
            organizations that represent the metal finishing industry, such as
            AESF (see above)  and the National Association of Metal Finishers
            (see below), and is involved in several joint programs, including an
            annual conference.   In addition, MFSA  publishes a monthly
            newsletter and has published a dozen technical papers to inform
            and assist its members.
National Association of Metal Finishers
(NAMF)
401 N. Michigan Avenue
Chicago, IL 60611-4267
Phone: (312)644-6610
Members:
Staff:
Budget:
Contact:

940
6
$750,000
Brad Parcells

             Founded in 1955, NAMF  represents management  executives  of
             firms  engaged  in  plating,  hard  chroming,  galvanizing,
             electroforming,  metalizing,  organic coating,  phosphating,  rust
             proofing, polishing, buffing,  anodizing, and  other forms of metal
             finishing.   NAMF  is  concerned  primarily with  management
             education,  development of  finishing standards, and  legislative
             issues.  In  addition, it  publishes Finishers'  Management, a trade
             magazine of the plating  and finishing  industry.   NAMF  also
             produces Finishing Line (monthly), Legislative  Line  (bi-monthly),
             and  NAMF Regulatory Compliance Manual.  NAMF holds  an
             annual trade show.
 SIC Code 34
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September 1995

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 Fabricated Metal Products
                                                            Sector Notebook Project
             Precision Metalforming Association (PMA)
             27027 Chardon Road
             Richmond Heights, OH 44143
             Phone: (216)585-8800
             Fax:  (216)585-3126	
            Members: 1,000
            Staff:  20
            Budget:  $3,000,000
            Contact:  JonE.Jenson
             Founded  in 1942,  PMA  represents  manufacturers  of  metal
             stampings, precision metal fabrications, and metal spinnings, and
             their suppliers.   PMA provides information and technical services
             to members.  It also presents numerous awards and publishes
             Metalforming, a  monthly magazine that addresses:  materials and
             equipment, electronics in metal forming and assembly, taxes, legal
             issues, and management.
             Society for Mining, Metallurgy, and
             Exploration, Inc. (SME)
             PO Box 625005
             Littleton, CO 80162
             Phone: (303)973-9550	
            Members: 20,000
            Staff:  31
            Budget: $3,700,000
            Contact:  Gary D. Howell
             Founded  in 1871, SME represents  individuals engaged  in the
             finding, exploitation, treatment, and marketing of all classes of
             minerals (metal ores, industrial minerals,  and  solid fuel)  except
             petroleum.  Additionally, it offers specialized education programs;
             and  compiles enrollment and  graduation  statistics from schools
             offering  engineering  degrees in  mining,  mineral,  mineral
             processing/metallurgical, geological, geophysical technology.
             United Steelworkers of America (USWA)
             5 Gateway Center
             Pittsburgh, PA 15222
             Phone: (412)562-2400
             Fax: (412)562-2445
            Members: 675,000
            Staff: 475
            Contact: George Becker
            Founded  in  1936,  this  association  has  absorbed  numerous
            associations for steel workers.  Currently, this agency publishes
            Steelabor ten  times a  year.   This  news magazine reports on
            legislation and regulation affecting the union, union activities at
            the national and chapter levels, economic developments, pension
            news, and information on safety and health.  USWA also publishes
            the  Steelworker  Old Time,  quarterly;  and  holds  a biennial
            convention.
September 1995
137
                             SIC Code 34

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Fabricated Metal Products
Sector Notebook Project
IX.   Contacts/Acknowledgments/Resource Materials/Bibliography and Other
      References

General Profile

Construction Materials, DOC, U.S. Industrial Outlook 1994.

Industry  Profile for the Metal Finishing Industry, Meridian Research Inc., U.S.
EPA/OPPT, June 24,1994.

1987 Census of Manufacturers Industry Series 34A: Metal Cans, Cutlery,
Handtoolsf U.S. Department of Commerce, Bureau of the Census, April 1990.
(MC87-I-34A)

1987 Census of Manufacturers Industry  Series 34B: Heating Apparatus and
Plumbing Fixtures, Bureau of the Census, April 1990.  (MC87-I-34B)

1987 Census of Manufacturers Industry  Series 34C: Fabricated Structural Metal
Products, Bureau of the Census, April 1990.  (MC87-I-34C)

1987 Census of Manufacturers Industry  Series 34D: Screw Machine Products,
Bureau of the Census, April 1990. (MC87-I-34D)


Process Description

Emissions From Metal Finishing Operations,  Draft Report, U.S. EPA, Office of
Research and Development, March 31,1995.

Hot Dip  Galvanized Coatings, American Society for Metals Committee on Hot
Dip Galvanized Coatings, Metals Handbook, 9th Edition, Volume 5.

Machining, American Society for Metals, Metals Handbook:  9th Edition,
Volume  16, 1989.

McGraw Hill Encyclopedia of Science and Technology, Volume 6, 1987.
 SIC Code 34
                                       138
       September 1995

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 Fabricated Metal Products
                                                             Sector Notebook Project
 Metals Handbook, Ninth  Edition; Volume 5,  Surface  Cleaning, Finishing, and
 Coating, 1982, American Society for Metals.

 Properties and Selection:  Stainless Steels, Tool Materials and Special Purpose
 Materials, American Society for Metals, Metals Handbook, 9th Edition,
 Volume 3, 1980.

 Selection  of Cleaning Process Metals, American  Society for Metals Committee
 on Selection of Cleaning Process, Handbook, 9th Edition.                '

 Surface Cleaning, Finishing, and Coating, American Society for Metals, Metals
 Handbook: 9th Edition, Volume 5, 1982.
 Regulatory Profile	

 U.S. EPA OPPTS Title III Section 313 Release Reporting Guidance:  Estimating
 Chemical Releases from Electroplating Operations, 1988.

 Guidance Manual for Electroplating and Metal Finishing Pretreatment
 Standards, U.S. EPA/Effluent Guidelines Division and Permits Division, 1984.

 Listing of Hazardous Waste (40  CFR 261.31 and 261.32): Identification and Listing
 of Hazardous Waste  Under RCRA, Subtitle C,  Section 3001, U.S. EPA, May 1980.

 Pollution Prevention	

 Guides to Pollution  Prevention:   The Metal Finishing Industry, U.S.  EPA,  ORD,
 October 1992.

 Minnesota Technical Assistance Program  Checklists for Identifying Waste
 Reduction Opportunities.

 Pollution  Prevention In Metal  Manufacturing:  Saving Money Through
 Pollution  Prevention, U.S.  EPA, OSW, October 1989.

 Pollution  Prevention Options  In Metal Fabricated Products Industries:   A
 Bibliographic Report, U.S. EPA,  OPPT, January 1992.

 Sustainable Industry:  Promoting Strategic Environmental Protection in the
 Industrial Sector, Phase 1 Report, U.S. EPA, OPPE, June 1994.

 Toxic  Chemical Release Inventory:  Clarification and Guidance for the  Metal
Fabrication Industry, U.S. EPA, OTS, 1990.
September 1995
139
SIC Code 34

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Fabricated Metal Products
                                  Sector Notebook Project
Contacts*
Name

Paul Beatty

Bob Benson


Marty Borruso


Jim Callier

Doug Fine


Marilyn Goode

Kris Goschen


Mardi Klevs

Larry Lins

John Robison


William Saas


Paul Shapiro


William Sonntag
Organization

U.S. EPA Region VII

U.S. EPA, Office of Policy,
Planning and Evaluation

American Electroplaters and
Surface Finishers Society

U.S. EPA Region VII

Massachusetts Department of
Environmental  Protection

U.S. EPA Office of Solid Waste

U.S. EPA Region VII, Southeast
Michigan Initiative

U.S. EPA SEMI  Coordinator

U.S. EPA Region V

U.S. EPA, Office of Pollution
Prevention and Toxics

Taskem, Inc., Metal Finishers
Suppliers'  Association

U.S. EPA, Office of Research and
Development

National Association of Metal
Finishers,  American Electroplaters
and Surface Finishers Society
Telephone

(913) 551-5089

(202) 260-8668


(718) 720-6646


(913) 551-7646

(617) 556-1049


(202) 260-6299

(913) 551-5078


(312) 353-5490

(216) 835-5200

(202) 260-3590


(216) 351-1500


(202) 260-4969


(202) 965-5190
     Many of the contacts listed above provided valuable information and comments during the
     development of this doucment. EPA appreciated this support and acknowledges that the
     indivduals listed do not necessarily endorse all statements made within this notebook.
 SIC Code 34
                                        140
                                         September 1995

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                                 APPENDIX A

       INSTRUCTIONS FOR DOWNLOADING THIS NOTEBOOK


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 of Enforcement and Compliance Assurance and the Office of Research and Development. The
 Network allows regulators, the regulated community, technical experts, and the general public to
 share information regarding: pollution prevention and innovative technologies; environmental
 enforcement and compliance assistance; laws, executive orders, regulations, and policies; points of
 contact for services and equipment; and other related topics. The Network welcomes receipt of
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      Or after  1997, (when EPA plans to have completed a restructuring of its web site) set
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(This page updated June 1997)
Appendix A

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