WNING .§'
.VI .4

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                                            SW3TSG
                OMAHA-COUNCIL BLUFFS

            SOLID WASTE MANAGEMENT PLAN

                    Status Report 1969
      This report (SW-3tsg), which has been reproduced
   exactly as received from the grantee with the exception
of a new title page and foreword, was prepared for the grantee
        by HENNINGSON,  DURHAM & RICHARDSON
    under State Solid Waste Planning Grant G05-UI-00041
      U.S. ENVIRONMENTAL PROTECTION AGENCY
              Solid Waste Management Office
                           1971

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This is an Environmental Protection Publication.

This publication is also in the Public Health Service numbered
series as Public Health Service Publication No. 2117.  Its
entry in two government publication series is the result of
a publishing interface reflecting the transfer of the Federal
solid waste management program from the U.S. Public Health
Service to the U.S. Environmental Protection Agency.

       Library of Congress Catalog Card No. 71-608770
         For sale by the Superintendent of Documents
              U.S. Government Printing Office
                 Washington, B.C. 20402
                      Price $2.25
                 Stock Number 5£t>2-0012

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                      OMAHA-COUNCIL BLUFFS
  *l
                  SOLID WASTE MANAGEMENT PLAN

  V
TO ENCOURAGE SYSTEMATIC PLANNING for better management of

the Nation's solid wastes, Congress in the 1965 Solid Waste Disposal

Act provided grant monies for the States for solid waste planning.

By June 1966, fourteen States had met the stipulations of the Act and

were  embarked upon the planning process with the help of  the Federal

funds. Today, almost every State has applied for and received a solid

waste planning grant.   From  each of the grants  the Federal government

expects two practical  results:   first,  a plan (and  report) for the State's

management of its  solid wastes; second, development of an agency for

the managing function.

       The present document publishes the  Omaha-Council Bluffs

interstate plan representing Douglas and Sarky Counties, Nebraska,

and Pottawattamie  County,  Iowa.  This was developed by the interstate

planning agency under a Federal solid waste management planning grant

that went into effect July  1,  1968.  The plan reported  on here is necessarily

based upon existing data,  technology, problems,  and objectives.  But, the
       LThe Solid Waste Disposal Act; Title II of Public Law 89-272, 89th
Congress,  S. 306, October 20, 1965.  Washington, U.S.  Government Printing
Office, 1966. 5 p.
       7
        Toftner, R. O. ,  D. D. Swavely,  W. T. Dehn, and B. L. Sweeney,
comps.  State solid waste planning grants, agencies, and progress--l970.
Public Health Service  Publication No. 2109.  Washington,  U.S. Government
Printing Office.  (In press.)
       3
        Toftner, R. O.  Developing a state solid waste management plan.
Public Health Service  Publication No. 2031.  Washington,  U.S. Government
Printing Office, 1970.  50 p.

                                 iii

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planning process is dynamic; future revision is an important part of

the process to take account of changing conditions and better data.

Moreover, a plan is not an end in itself.  Its formulation is  the key

to action: to legislation, standards, technical assistance, public

relations, and enforcement.

       Besides  providing the interstate planning  agency with a guide

for action, the Omaha-Council Bluffs plan will help to guide regional

solid waste planning and subsequent implementation.   The plan can

also provide  support for improved local legislation related to solid

waste management.

       The plan is designed, therefore, to:  (1) begin the planning

process; (2) establish policies and procedures to guide the interstate

planning agency; (3) guide regional planning; (4) provide a documented

base for improved solid waste ordinances and operating regulations.

With these objectives in mind,  this plan report presents and analyzes

pertinent solid waste data,  identifies  problems indicated by the data,

sets objectives  that if achieved would solve identified problems, and

finally, proposes  immediate,  intermediate, and long-range measures

for achieving  objectives.  This plan should thus provide the interstate

agency with an invaluable management tool with which to begin  solving

the solid waste  problems in the Omaha-Council Bluffs metropolitan area.
                                --RICHARD D. VAUGHAN
                                  Assistant Surgeon General
                                  Acting Commissioner
                                  Solid Waste Management Office
                                  IV

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                 ACKNOWLEDGEMENT
     The development of this report has been made pleasur-




 able by the cooperation of many persons and organizations that




 were contacted during the study period.




     Especially grateful acknowledgement is rendered to




 Mr. Victor E.  Ziegler, P. E. who is the MAPA Environ-




 mental Health Director.  His thoughtful comments, particu-




 larly during the final editing, were valuable and appreciated.




     Also grateful acknowledgement is  rendered to the mem-




bers of the  Technical Review Committee, who met monthly




during the course of the study.  This committee listened to




many hours of presentations, offered their criticism and ad-




vice, and in general acted as a knowledgeable technical




sounding Board.   Their assistance and  enthusiastic coopera-




tion have made a significant  contribution to this report.




    This solid waste disposal planning project was




supported in part by a grant  from the Public Health Service,




Department of Health, Education and Welfare.




Grant Number G05-U1-00041.

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                 METROPOLITAN AREA PLANNING AGENCY
                     COUNCIL OF ELECTED OFFICIALS
 President
 Vice President
 Harry Andersen
 Richard Anderson
 Cecil Blum
 William V.  Brooks
 George Buglewicz *
 Marvin G. Ellis
 Donald Franksen
 Arthur Gottsch
 Ronald Grear
 Robert Haworth
 H. F. Jacobberger
 Russell Johns
 Joseph Wager
 Lynn L. Landgren
 Colonel Anson D. Marston
 Robert S. Metzler
 John Neuberger
 Al C.  Pawloski
 Lyle Plugge
 Omar  E.  Robb
 Eugene Leahy
 Thomas Thomsen
 Robert Walton
 Msgr.  Nicholas Wegner
 *  Officially Designated Rep
                                      Lynn L. Landgren
                                      Donald Franksen
       Mayor of Millard, Nebraska
       Mayor of Gretna, Nebraska
       Mayor of Walnut, Iowa
       Chairman, Sarpy County Board of Commissioners
       Chairman, Douglas County Board of Commissioners
       President, Bellevue School Board
       Mayor of Council Bluffs, Iowa
       Mayor of Elkhorn, Nebraska
       Omaha Airport Authority
       Mayor of Bellevue, Nebraska
       President, Omaha City  Council
       Mayor of Bennington, Nebraska
       Mayor of Ralston, Nebraska
       Mayor of Papillion, Nebraska
       Chairman, Omaha Planning Board
       President, Millard School Board
       Papio Watershed Board
       Chairman, Council Bluffs Planning Commission
       President, Ralston School Board
       Mayor of La Vista, Nebraska
       Mayor of Omaha, Nebraska
       Lewis Central School Board
       Chairman, Pottawattamie County Board of Supervisors
       Chairman, Boys Town Village Board of Trustees
   resentative. . .  Mr. Jack Cavanaugh
Chairman
Vice Chairman
Sec retary
Treasurer
BOARD OF DIRECTORS
       Robert S.  Walton
       George Buglewicz
       Al C.  Pawloski
       William V. Brooks
William V. Brooks
George Buglewicz
Donald Franksen
H. F.  Jacobberger
Harry Andersen
   MEMBERS
       Col.  Anson Marston
       Al C.  Pawloski
       Eugene Leahy
       Robert Walton
O. A.  Kinney,  Jr.
Hal L. Taylor
Victor E.  Ziegler
Larry Snail
Gerald Tartoni
Frank E.  Keele
Robert Tallant
Dorothy Renstrom
Donna  Collatz
Arleen  Winkler
Kirk Crane
    MAPA STAFF
       Executive Director
       Assistant to the Director
       Environmental Health Director
       Comprehensive Planning Director
       Director of Urban Affairs and Trans.
       Planning Technician
       Planning Technician
       Administrative Secretary
       Secretary
       Bookkeeper-Secretary
       Planning Aide

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                            TOPICAL SUMMARY

 PART ONE - GENERAL

 The Study Area consists of all of Pottawattamie County, Iowa and Douglas and
 %irpy Counties,  Nebraska, an area of slightly more than 1500 square miles,
 containing a present population of approximately 529, 000.   By 1995 this population
 is expected to increase to approximately 767, 000.

 All existing  solid waste disposal facilities open to the public, and disposal facil-
 ities used by solid waste collectors collecting from the public were examined
 and  rated.  There are  21 of these facilities,  seven serve the urban area contain-
 ing approximately 95% of the population and 14 serve the remaining rural areas
 or were very small facilities in the urban area.

 All of the facilities have some deficiencies, some of which could be corrected,
 but many of the facilities must be classified as unregulated open burning dumps.

 The  basic  problem in solid waste management is the apathy of the general public,
 and the unglamorous nature of solid waste disposal.  Until  recently, few people
 were concerned with these matters.  Except in a few cases, little professional
 skill has been applied to the storage,  collection, transportation and disposal of
 solid wastes. As a result, the services being offered are often inadequate in
 scope and  execution, and cost more than first class,  well organized services.

 The  technology for storage,  collection, transportation, and disposal of solid
 waste in an efficient, sanitary, nuisance free  and economical manner is avail-
 able and ready for use,  when the public demands proper service and govern-
 mental officials supply the necessary management.

 PART TWO - SURVEY OF SOLID WASTE

 Extensive surveys were made to determine the quantity and characteristics of
 the present and future solid wastes in the  Study Area.  Included were  surveillances
 of the seven major public disposal facilities,  commercial and industrial surveys,
 and special studies of special wastes.  These  surveys were  analyzed using
 systems analysis  methods, and electronic data processing equipment.  As a
 result, information was obtained describing the wastes as  a function of: time
 and day of  delivery, vehicles used for hauling, classification of haulers, political
 subdivision of the origins, geographic areas of origins,  centroids, potential
 disposal processes, types of wastes by waste  classification, volumes and weights
 of wastes,  compaction factors and seasonal variations.  The information obtained
is presented in graphic and tabular form and was used in developing the recom-
mended facilities.

The 1968 annual volume and weight of materials which should have been disposed
of at public facilities was equal to approximately one (1) million  cubic yards and
 and approximately 700,000 tons per year.  By 1995 these quantities are expected
                                      VI1

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to increase to 1, 600, 000 cubic yards and 1, 200, 000 tons.  If accumulated, these
quantities would represent a volume equal to approximately 21, 000 acre feet
and 26 million tons.

In addition to these materials which can be expected to be delivered to public
disposal facilities, a very large volume and tonnage of material will continue
to be disposed of at private facilities serving the disposal needs of the facility
operator.

PART THREE - DISPOSAL FACILITIES

The  sanitary landfill method of disposal is  recommended for the solid wastes
produced in the Study Area.  Reasons and conditions favoring this recommenda-
tion  are:

         1.      Adequate land is available.

         2.      The method has been proven satisfactory where properly
                operated.

         3.      The method can meet all health and sanitation requirements
                and be aesthetically pleasing.

         4.      The method is adaptable to varying quantities  and peak or
                slack rates.

         5.      The method is the most economical.

Criteria for the selection of general areas  for  sanitary landfills is presented.
The  items  include:

         1.      Minimum driving time and distance to site area.

         2.      Present land use compatible with sanitary landfilling.

         3.      Accessible to major highways  or arterial  streets.

         4.      Economical land costs.

         5.      General topography, including terrain, ground cover, ground
                water and major subsurface conditions must be favorable.

         6.      Suitable earth cover must be available.

Economic comparisons were made  of potential site areas and  combinations of
site  areas,  through the use of simulation methods, to determine which combina-
tion  should be recommended.  Consideration was given to  both the cost of hauling
waste products to disposal facilities and the operation of the facilities in  deter-
mining the total cost to the  community.

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Four general site areas in the urban area are recommended;

         1.      Site Area No. 1 - Vicinity of Interstate 80 and Nebraska
                                  Highway 50 in Sarpy County.

         2.      Site Area No. 3 - West of the present Douglas County
                                  Sanitary Landfill Site in the general
                                  vicinity of 120th & Fort Streets in
                                  Douglas County.

         3,      Site Area No. 5 - Between Lake Manawa and the Missouri
                                  River,  South  of U. S. 275, in Council Bluffs.

         4.      Site Area No. 7 - North of Dodge  Park,  near the Missouri
                                  River, north of Omaha in Douglas County.

These general site areas, containing a total of approximately 1,000 acres, will
be needed to fill the solid waste products  expected from the year 1970 to the
year 1995.

In addition to the four general areas for sites  to serve the urban area, one addi-
tional site is recommended to serve eastern Pottawattamie County.  The general
area for this site is in the vicinity of Hancock, Iowa.  To make this single site
economical for the small communities and rural population,  an organized collec-
tion service is recommended.

The cost of the initial capital expenditures for the four urban sites and one rural
site, including land,  equipment purchase, and initial development, is approxim-
ately $2,200,000.

The total cost of operation, including  initial capital expenditures plus operation,
is approximately $1. 40 per ton.   This is less  than what is currently being spent
for some lesser facilities,  and estimated to be less  than what other inadequate
facilities would cost if their operations were brought up to reasonable standards.

PART FOUR - ORGANIZATION FOR SOLID WASTE DISPOSAL

The recommended organizational structure for the disposal of solid waste is a
single,  non-profit, public agency.  This agency would be formed for the purpose
of operating and/or managing all  public solid waste disposal facilities in the
three county MAPA area,  as  one  coordinated activity, in accordance with a
Master Plan for area-wide solid waste disposal.  It would operate  for and on
behalf of all of the member municipalities for their mutual benefit.

Each member would agree to the  Master Plan and pass any ordinances or regula-
tions necessary to implement the plan and to grant to the agency exclusive operat-
ing authority within their jurisdiction.
                                    IX

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Fees would be charged at all agency facilities,  for disposal services.  These
foos would be uniform at all facilities,  non-discriminating,  and adequate in
amount to produce the necessary revenue to make the entire disposal operations
self-supporting.

The purchase of land, capital improvements to the land and initial complement     .
of equipment would be paid for with the proceeds  of revenue bond issues.  The
user fees would pay for the bond debt service, debt service reserve, operation
and maintenance, equipment replacement, site improvements, miscellaneous
and incidental expenses, management and overhead.

The agency membership would consist of one representative of each participating
city, town,  village and county.  The agency's policy  and governing body  would
be a Board of Directors consisting of one member from each of the three counties,
three additional members  representing the  small communities in each of the
throe counties, and one member each from the major cities.  Each Board Member
would cast  one vote for each 50, 000 population in the jurisdiction he represented.

An Inter-governmental agreement creating the recommended agency is presented
in the report.  Also  presented are proposed ordinances for the collection and
disposal of solid wastes which the various municipalities may find helpful.  They
contain the essential technical elements for adequate solid waste matters and
certain procedural items tailored for a municipality participating in an agency
operated solid waste system.

State and Local Legislation is reviewed and recommendations are made  to
improve the legal basis for solid waste management.

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                        TABLE OF CONTENTS
Part One                    Description
GENERAL
A. Scope
B. Definition of Terms
C. Description of the Study Area
1. General
2. Population
3. Land Use
D. Existing Solid Waste Facilities
1. Name and Location
2. Survey of Existing Facilities
E. Need For Solid Waste Management
F. Present Technology
1. General
2. Collection Systems
3. Transportation Systems
4. Disposal Systems
Part Two
SURVEY OF SOLID WASTE
A. General
B. Commercial and Industrial Surveys
1. Surveys
2. Waste Quantity
3. Total Industrial & Commercial Waste
C. Residential Survey
D. Special Studies
1. General
2. Automobiles and Scrap Metal
3. Special Tree Waste
4. Meat -packing Industry Waste
5. Disposal of Feedlot Waste

I -
I -
I -
I -
I -
I -
I -
I -
I -
I -
I -
I -
I -
I -
I -

II -
II -
II -
II -
II -
II -
II -
II -
II -
II -
II -
II -
II -

1
2
5
5
7
9
9
9
12
18
21
21
21
23
25

1
1
1
1
2
2
6
8
8
9
14
17
20
                              XI

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                          TABLE OF CONTENTS (continued)

Part Two                     Description                          Page

         E.    Landfill Surveys                                    II _ 23

               1.    General                                      II - 23
               2.    Computer Programs                          II - 30

         F,    Volume,  Weight and Vehicle Analysis               II - 52
         G.    Origin of Landfill Waste                            II - 61
         H.    Present Quantities                                  11-63

               1.    Measured Area                               II - 63
               2.    Total Study Area                              U - 67

         I.     Future Quantities                                   II - 67

Part Three

         SOLID WASTE DISPOSAL FACILITIES

         A.    General                                            III - 1
         B.    Recommended Method of Disposal                   IH _ 2
         C.    Selecting General Areas For Solid Waste            III - 2
               Disposal Facilities

               1.    General                                      III - 2
               2.    Driving Time and Distance                    III - 2
               3.    Land Use                                     III - 5
               4.    Accessibility                                 III - 5
               5.    Land Cost                                    in - 5
               6.    General Topography                          III - 5
               7.    Earth for Cover Material                     III - 6

         D.    Selection of Proposed Facilities                     III - 6

               1.    Transfer  Station                              III - 6
               2.    Economic Simulations of Potential
                    Sanitary Landfill Sites                        III - 13
               3.    Domestic Solid Waste Collection and Dis-
                    posal in Eastern Pottawattamie County        in - 23
              4.    Sanitary Landfill Cost Estimates              III - 31

                    a      General                                III - 31
                    b     Basic Cost Data                         III - 32
                    c      Annual Cost                             III - 33
                                   XI1

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                          TABLE OF CONTENTS (continued)

Part Three                    Description                         Page
              4.    (continued)
                    d.    Fixed and Variable Annual Costs         III - 34
                    i\    Quantities for Unit and Total Cost        III - 34
                    f.     Unit and Total Costs of Operation        HI - 34
                    g.    Bond Debt Service Reserve              III - 3S
                    h.    Summary of Unit Costs                  III - 35
                    i.     Individual Site Data                      HI - 35

              5.    Summary - Resulting Site Combination^        III - 42
              6.    Recommended Disposal Facilities              III - 45
              7.    Recommended Disposal Fees                  III - 48

         E.   Site Development                                   III - 50

              1.    Development of Flat Site                      IU _ 50
              2.    Development of a Hilly Site                    III - 55

         F.   Final Use and Iterim Use of Sanitary Landfill Sites   IIJ - 5§

Part Four

         ORGANIZATION FOR SOLID WASTE

         A.   General                                            IV - 1
         B.   Collection of Solid Waste                            IV - 1
         C.   Legal Status of the Agency                           IV - 1
         D.   Membership                                        IV - 7
         E.   Formation of the Agency                            IV - 7
         F.   Operation of the  Agency                             IV - 8
         G.   Financing                                           IV - 10

              1.    Disposal Service                              IV -  10
                    a.     Revenue Bonds                           IV -  10
                    b.     Operating Revenue                       IV -  21
                    c.     Revenue Required                       IV -  21
                    d.    Income                                  IV -  22
                    e.     Disposal Fees                           IV -  22

              2.    Collection  System                              IV -  22

         H.    Interim Activities                                   IV - 23
         I.     State Legislation                                    IV - 24
              1.    Financing and Eminent  Domain                IV - 24
              2.    Authority of the Various Subdivisions of the     IV - 25
                     State
                                  Xlll

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Part Four
         J.
         K.
         L.
         M.

APPENDIX
            TABLE OF CONTENTS (continued)

                Description                             Page

    2.   (Continued)
          a.     Collection of Garbage and Refuse          IV -  25
                  in Iowa Cities and Towns
          b.     Collection of Garbage and Refuse in        IV -  31
                 Iowa and Nebraska Counties
          c.     County Disposal of Refuse in Nebraska    IV -  31

    3.    State Regulatory Agency                        IV -  31

    Local Legislation                                    IV -  33

    1.    Disposal Ordinance                             IV-  33
    2.    Collection Ordinance                           IV -  33
    3.    Junked Automobiles                             IV -  33

    Sanitary Landfill Standards                           IV -  34
    Alternate Possibilities                               IV -  34
    1.    Organizational Structures                       jy -  34
    2.    Operation of Agency Facilities                  jy -  36

    Federal Participation                                IV -  37
         LIST OF TABLES.  FIGURES. DOCUMENTS AND EXHIBITS
Part
One
Table, Figure
or Document
Table I - 1
Table I - 2
          Table 1-3

          Table 1-4

          Figure I -  1
          Figure 1-2
          Figxire 1-3
          Figure 1-4
            Title                 Page Number
Existing Land Use                        I - 11
Major and Minor Public Disposal         1-13
   Facilities (2 pages)
Sanitary Landfill "Must" Items and       1-17
   Ratings
Inventory of Collection Practice           1-24

Metropolitan Solid Waste Study Area      1-6
Population Trends                        1-8
Existing Disposal Sites                   I - 10
Comparing Solid Waste Collection        1-20
  and Disposal Cost With Other
  Services and Utilities
          Exhibit I - 1    Sample  Land Disposal Site Investigation
                           Report form USPHS
          Exhibit 1-2    Samples Tentative Landfill Rating Form
                                   XIV

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LIST OF TABLES. FIGURES.  DOCUMENTS AND EXHIBITS (continued)
  Table,  Figure
  or Document
  Table II -  1

  Table II -  2

  Table II -  3

  Table II -  4
  Table II -  5

  Table II -  6

  Table II -  7
  Table II -  8
                   Title
                                  Page Number
  Table
  Table
  Table
  Table
  Table
  Table
  Table
  Table
  Table
  Table
  Table
  Table
  Table
  Table
  Table
II - 9
II -10
11-11
II -12
II -13
II -14
II -15
11-16
11-17
II -18
II -19
II -20
II -21
II -22
II -23
  Table II -24

  Table II -25
  Table II -26
  Figure II -1
  Figure II -2

  Figure II -3

  Figure II -4
 Commercial and Industrial Survey-       II - 3
   Material Quantities Per Employee
 Commercial and Industrial Survey-       II - 4
   Material Quantities
 Summary of Commercial and Industrial   II - 5
   Annual Waste Quantities
 Meat-packing Industry Waste Quantities   11-19
 Annual Daily Manure Production and      11-21
   Composition
 Estimated Annual Manure Production -    11-22
   Commercial Feedlots in Study Area
 Days and Dates for Landfill Surveys       II - 24
 Materials, Compaction Factors,          II - 33
   Seasonal Factors and Unit Weights
 Computer Program A                    11-36
 Computer Program B                    11-37
 Computer Program C                    H - 39
 Computer Program D,  Pages 1 and 2     11-40
 Computer  Program E                    11-42
, Computer Program F                    11-43
 Computer Program G                    11-44
 Computer Program H,  Pages 1 and 2     11-45
 Computer Program I                     11-49
 Computer Program J                     11-49
 Computer Program K                    11-49
 Computer Program L                    11-50
 Computer Program M                    11-51
 Computer Program N                    11-51
 Comparison of Waste as Received From   U - 62
   Political subdivision
 Annual Quantities and Accumulations      II - 64
   of Refuse for the Measured Area
 Major Categories of Waste                II - 66
 Annual Quantities and Accumulations
   of Refuse for the Total Study Area       11-68

 Disposal Surveillance Questionaire        II - 26
 Comparing the Several Sites for Waste    II _ 53
   Quantities and Vehicular Traffic
 Comparing the Vehicle Types for          11-54
  Waste Quantities and Vehicular Traffic
 Comparing the Hauler Types for Waste    11-56
   Quantities and Vehicular Traffic
                          xv

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Part
Two
Parl
Three
 LIST OF TABLES. FIGURES. DOCUMENTS AND EXHIBITS (continued)


                                                    Page Number       *
Table,  Figure
or Document
Title
          Figure II - 5    Comparing the Seven Days of the
                            Week for Waste Quantities and
                            Vehicular Traffic
          Figure II - 6    Comparing the Hours of the Day for
                            Waste Quantities and  Vehicular
                            Traffic
          Figure II - 7    Comparing the Hours of the Day and
                            Vehicle Count for the Types  of
                            Vehicles

          Exhibit II  -  1    Elm Tree Statistical Information
          Exhibit II  -  2    Unit Weights
Table III - 1

Table III - 2
Table III - 3
Table III - 4
Table III - 5
          Table III - 6
          Table III -  7
          Table III -  8
          Table III -  9
          Table III -10
          Figure III -  1

          Figure III -  2
          Figure III -  3
          Figure III -  4
          Figure III -  5

          Exhibit III - 1
          Exhibit III - 2
          Exhibit III - 3
                Transfer Station - Basic Data for
                  Cost Estimate
                Economic Site Simulations
                Economic Site Simulations
                Economic Simulation No. 98 (typical)
                Eastern Pottawattamie County Domestic
                  Refuse Collection and Preliminary
                  Daily Work Schedule
                Cost Estimate, Domestic Waste
                  Collection,  Eastern Pottawattamie
                  County
                Recap - Cost Estimate
                Basic  Cost Data For Sites 1, 3, 5, 7 and 8
                Basic  Site Data For Sites 1,3,5,7 and 8
                Comparative Figures - Five  Site
                  Combinations

                Potential Disposal Site Locations and
                  Quantities by Geographic Areas
                Transfer Station
                Recommended Sanitary Landfills
                Typical Flat Site Operation
                Typical Hilly Site

                Site Simulation No. 65
                Site Simulation No. 87
                Site Simulation No. 92
                                                           II - 58
                                                           II - 59
                                                           II - 60
                                  III - 11

                                  III - 14
                                  HI - 17
                                  IH - 19
                                  III - 27
                                                           III - 30
                                                           III - 38
                                                           III - 39
                                                           HI - 41
                                                           HI - 43
                                                           IH - 3

                                                           III - 8
                                                           IH - 21
                                                           III - 53
                                                           IH - 57
                                   xvi

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      LIST OF TABLES. FIGURES. DOCUMENTS AND EXHIBITS  (continued)
Part      Table, Figure
Throe     or Document

          Exhibit III - 4
          Exhibit m -  5
          Exhibit III - 6
          E xhibit in - 7
          Exhibit III - 8
             Title
Page Number
Cost Estimate - Solid Waste
  Disposal Facilities, Sanitary
  Landfil] Sites 3,5 and 7
Cost Estimate - Solid Waste
  Disposal Facilities, Sanitary
  Landfill Sites 3 and 5
Cost Estimate - Solid Waste
  Disposal Facilities, Sanitary
  Landfill Sites 1,  3 and 5
Cost Estimate - Solid Waste
  Disposal Facilities, Sanitary
  Landfill Sites 1,3, 5 and 7
Cost Estimate - Solid Waste
  Disposal Facility, E.  Pottawattamie
  County Sanitary Landfill Site No.  8.
          Table IV - 1
          Figure IV - 1
          Document
          IV - 1
          IV -  2
          IV -  3
          IV - 4
          Exhibit  IV - 1
Revenue Requirement  and Income       IV - 21
  for Agency Disposal of Solid Waste

Proposed Organizational Structure       IV - 9
  for the Agency - 1969
Intergovernmental Agreement Creating   IV - 2
  the Omaha-Council Bluffs Metropolitan
  Area Solid Waste Agency
Proposed Refuse Disposal Ordinance     IV - 11
  for Cities Contracting with the Ormha-
  Council Bluffs Metropolitan Area
  Solid Waste Agency
Proposed Refuse Collection Ordinance    IV - 17
  for Cities,  Towns,  and Villages
  Contracting with the Omaha - Council
  B luffs  Metropolitan Solid Waste  Agency
Proposed Solid Waste Disposal Act       IV - 26

   Disposal Fees
                                  XVll

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                        PART ONE - GENERAL

         SCOPE.   The objective of this study is to make a detailed analysis
 of solid waste disposal in the Study Area and to make recommendations for
 the most feasible program of disposal, both for the present and for the fore-
 seeable future.

 The principal items of study and recommendation include the following:

          1.       Determination of present solid waste quantities, character-
 istics,  and origin by performing the following:

                  &.    Reviewing and analyzing existing records.

                  b.    Surveying major disposal facilities.

                  £.    Surveying minor disposal facilities.

                  d.    Determining major waste categories.

                  £.    Locating and surveying major waste contributors.

                  f_.    Surveying and  studying the  effect of backyard inciner-
                       ation on domestic wastes.

                  £.    Surveying and  studying governmental subdivision pro-
                       cedures and wastes.

                  h.    Determining quantities of special problem wastes.

         2.       Determination of future quantities of solid waste based on pres-
 ent quantities, land use and population projections  to 1995.

         3.       Determination of centroids of the various solid  wastes gener-
 ated within the Metropolitan Study Area.

         4.       Feasibility of storage or transfer stations.

         5.       Study of methods  available for  solid waste disposal and recom-
 mend method of appropriate future  solid waste disposal.

         6.       Study of existing laws regulating  solid waste disposal and recom-
 mend appropriate legislation.

         7.       Study of potential financing of recommended solid waste dis-
 posal facility.

         8.      Study of existing administrative procedures and recommend es-
tablishment of appropriate  solid waste  management program.

                                     1-1

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B_.	DEFINITION OF TERMS

         1.       Abandoned Vehicles.  Passenger automobiles,  trucks and
trailers  that are no longer useful as such which have been abandoned on
streets,  highways and other public places.

         2.       Bulky Waste.  Large items of refuse such as appliances,
furniture, large auto parts,  trees and branches, stumps, and similar large
items not easily crushed or reduced in volume using light landfilling equip-
ment.

         3.       Commercial Waste.  All  solid waste originating in commer-
cial establishments.

         4.       Composting.  A process for biological decomposition of or-
ganic waste in a nuisance-free manner through controlled environment either
aerobic or anaerobic, producing a stable residue which may be used as a soil
conditioner.

         5.       Construction and Demolition Wastes.  Waste building ma-
terials and rubble resulting from construction,  remodeling, repair,  and
demolition operations on houses,  commercial buildings,  pavements and other
structures.

         6.       Disposal Area.  A site, location, tract of land, area, build-
ing, structures,  or premises used or intended to be used for  partial and/or
total refuse disposal.

         7.       Domestic Waste.  All types  of refuse which normally origi-
nate in the residential household or apartment house.

         8.       Dump, Open .  The consolidation of waste from one or more
sources at a central out-of-doors disposal  area, which has little or no manage-
ment and which does not conform to the requirements of a landfill or sanitary
landfill.

         9.       Dump, Open Burning.  An open dump where burning is permit-
ted in an uncontrolled manner.

         10.      Dump, Controlled Open Burning.  An open dump where burn-
ing is controlled by some responsible person.  Burning is not confined to an in-
cinerator but is practiced in the open on the ground.

         11.      Dump, Controlled.  See Landfill.
                                   1-2

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          12.      Garbage.  Garbage is the solid or semi-solid animal and
 vegetable waste resulting from the handling, preparation, cooking and ser-
 ving of foods,  including cans, bottles and cartons in which it was received
 and wrappings in which it may be placed for disposal.  Garbage does not in-
 clude  commercial and industrial waste from meat packing plants, food proces-
 sjng plants such as canneries and crop wastes from farms,  nor market wastes
 which originate in wholesale and retail stores or markets engaged in the stor-
 age, processing and selling of food products.

          13.      Incineration.  The controlled process of burning solid,
 semi-solid, liquid or gaseous combustible wastes in an enclosed device,
 producing an inoffensive gas and a sterile residue containing little or no com-
 bustible material.  The process is used to reduce the  volume or weight of
 waste  material or to change the characteristics of hazardous wastes to a safer
 form.

          14.      Industrial Waste.  All solid waste originating in industrial
 establishments.

          15.      Landfill.  Same as a  sanitary landfill,  except, cover material
 is applied from time to time as required, instead of daily or more frequently.
 To be  acceptable,  landfills must  be restricted to inert, non-combustible, non-
 putrescible solid waste materials.

          16.      On-Site Disposal.  The disposal or partial disposal of solid
 wastes on the premises where it  was originated, including incineration or
 burial.

          17.      Pollution.  The  contamination of any air, water or land
so as to create a nuisance or render such air, water or land unclean or
 noxious,  or impure so as to be actually or potentially harmful  or detrimental
 or injurious to public health, safety,  or welfare, to domestic,  commercial, in-
 dustrial or recreational use, or to livestock, wild animals,  birds,  fish,  or other
 aquatic life or to plant life.

         18.      Refuse. Solid waste.

         19.      Residue.  Solid material remaining after burning,  including
 ash, metal,  glass,  ceramics, plastics,  and unburned combustibles.

         20.     Rubbish.  Non-putrescible wastes, such as cardboard, paper,
 tin cans,  wood, glass, bedding, crockery or litter of any kind.

         21.     Salvage, Auto.   A commercial enterprise  engaged in the pur-
 chase  of obsolete or damaged motor vehicles for the removal and resale of usable
parts and the reclaiming of valuable metals.
                                    1-3

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         22.      Salvage, Melal.  A commercial enterprise engaged in the
purchase of salvaged metals for resale, or processing and resale of these
metals to metal consuming industry.

         23.      Salvaging.   The controlled removal of reusable materials.
Not to be confused with scavenging.

         24.      Sanitary Landfill.  A controlled method of disposing of
refuse on land without creating air, land or water pollution or nuisances or
hazards  to public health or safety, by utilizing the principles  of engineering
to confine the refuse to the smallest practical volume, and to cover it with a
layer of  earth at the conclusion of eacy day's operation,  or at such more fre-
quent intervals as may be necessary.

         25.      Scavenging.  The  uncontrolled picking of materials.  Not
to be confused with salvaging.

         26.      Street Refuse.  Material picked up by manual and mechani-
cal sweeping of streets and sidewalks, litter from public receptacles,  and
dirt removed from catch basins.

         27.      Special Wastes.  Hazardous wastes by reason of their path-
ological, explosive, radioactive, or toxic nature; or wastes which require
special treatment prior  to disposal in ordinary disposal facilities, or special
facilities.

         28.      Solid Waste.  Waste is unwanted or discarded materials re-
sulting from commercial, industrial and agricultural operations and normal
community activities.  Wastes include solids,  liquids and gases.  Wastes which
are solid or  semi-solid  containing insufficient liquid to be free-flowing are
classed as  solid waste.

Solid waste is refuse and includes in part the following:  garbage; rubbish;
ashes and other residue after burning; street refuse; dead animals; animal
waste; abandoned vehicles; agricultural,  commercial and industrial waste;
construction and demolition waste;  sewage treatment residue.

         29.      Yard Rubbish.  Prumings,  grass clippings,  weeds, leaves,
and general yard and garden wastes.
                                    1-4

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C^	DESCRIPTION OF STUDY AREA

         1.       General.   The Study Area as established for purposes  of
ttiis report includes all of the Standard Metropolitan Statistical Area which
includes the  counties of Douglas and Sarpy in Nebraska and the County of
Pottawattamie in Iowa.  Basically,  the Study Area comprises approximately
1, 530 square miles encompassing the Major Metropolitan Areas of Omaha,
Bellevue, and Council Bluffs as shown in Figure 1-1.  Specifically, the Study
Area includes the following Governmental Jurisdiction or Political Units:

Douglas County:

         Bennington, Boys Town, Elk City, Elkhorn, Irvington,  Millard,
         Omaha, Ralston, Valley, Waterloo.

Sarpy County:

         Bellevue,  Chalco, Gretna,  LaPlatte, La Vista,  Meadow, Melia,
         Offutt, Papillion, Springfield.

Pottawattamie County:

         Avoca, Bentley, Carson, Carter Lake,  Council Bluffs,  Crescent,
         Dumfries,  Hancock, Honey Creek, Loveland,  Macedonia, McClelland,
         Minden, Neola,  Oakland, Quick, Treynor,  Underwood,  Walnut,
         Weston.

Omaha,  the principal city in the Study Area and largest city in the State  of
Nebraska, is predominantly a trade, service and processing center for the
surrounding  agricultural region.  In general,  the Study Area is served by Inter-
state Highways 1-29 and 1-80, numerous other State and Federal Highways,  and
major air line and  rail transportation systems which provide over-night access
to Chicago,  Denver,  St.  Louis,  Minneapolis/St.  Paul and Kansas  City.

The Study Area economy has been expanded and strengthened in recent years
as a result of several developments including the expansion of headquarters
office  operations in the insurance and utility fields,  the  expansion of govern-
mental activities - particularly the Strategic Air Command and recent acqui-
sition of new industries.

The Study Area is located near  the geographic center of the United States and has
grown and prospered as a result of this advantageous location.  Additional impe-
tus to  the growing communities within the Study Area were furnished by  the
rapid mechanization of agriculture and the rise  of the cattle industry.  This
agricultural base created the stockyards, grain markets,  and food processing
industries which are an important segment of the Study Area economy.
                                     1-5

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                         IOWA
NEBRASKA
                        METROPOLITAN
                  SOLID WASTE STUDY AREA
                  1-6
                                      Fl GU RE  I - I

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 This area does not depend solely on agricultural production, but enjoys broad
 diversification of its economic base; with other activities such as manufactur-
 ing, transportation,  communication,  services, wholesale trade and insurance
 favilities being of almost equal importance.  Basic employment therefore is
 diversified among the various economic activities with no single unit over-
 balancing the others,  giving a sound basis for all economic activities.

 Judging from the population studies,  the basic employment  studies and the dis-
 tribution  of employment among the industries, it appears inevitable that there
 will be marked growth in the manufacturing field.   The trend toward steady,  con-
 stant growth rather than periodic spurts of growth  should produce a consistent
 overall development in all phases of the economic base.

 The geographic location should continue to be a tremendous advantage, provi-
 ded the communities in the Study Area continue to capitalize on the trans-
 continental interstate highway program and the federal airways and air terminal
 programs.

 The climate  of the Study Area is marked by seasonal variations in temperature
 and precipitation.  The average annual temperature is a comfortable 51.1 de-
 grees.  Mid-summer average daytime temperatures range from 85 to 87 de-
 grees.  Daytime winter temperatures average from 31 to 32 degrees, with night-
 time winter temperatures  averaging from 15 to 19 degrees.  Humidity ranges
 from 55 to 60 percent from noon to midnight, and 75 percent to 80 percent from
 midnight to noon.  The average normal precipitation is 28. 83 inches,  75  per-
 cent of which falls between April and September.  The average normal snowfall
 is 28. 50 inches.   Northwest winds predominate during the -winter months
whereas,  the  summer winds prevail from the south and southeast.
The Standard Metropolitan Area utilities followed the national pattern of steady
growth since I960.  Electric sales were up 59% over I960; gas usage increased
by 34% and telephones in use and water  pumped showed similar increase.

         2.      Population.  An analysis of the past, present and future pop-
ulation trends of a community are a necessary prerequisite to planning future
solid waste facilities.  The quantity, type and volume of solid waste that is gen-
erated, and for which provisions for disposal  must be made, are related to the
population and  the associated commerce and industry, which support the popula-
tion.

The  population projections for the Study Area  from I960 to 1995 were developed
by the  Omaha-Council Bluffs MAPA and furnished for use in this study.  These
figures show a steady increase from 458, 000 in I960 to 766, 600 in 1995, which
is equal to an average annual increase of 8,807 persons or 1. 9% per year, based
on I960.  See Figure 1-2 for Population  Trends.
                                  1-7

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 780,000
 740.000
700,000
 660,000
 620,000
 580,000
540,000
500.000
 460.000
      1960
                        546
                    528,800^
                    z
              MSI
          400
                                \
                                                634,500
                                                      *'
                                               	A
                                                              ^
1965    1968  1970
1975         1980
  YEAR
                                                                        722.500.
                                                                            •" \
                                                                         A
                                                                    A
1985
                                                                                    766,600,
1990
1995
                                                       POPULATION   TRENDS
                                                                         FIGURE  T- 2

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         3.       Land Use.  Table 1-1 indicates present land use (by acres)
for the Study Area. It should be emphasized that the land uses as shown are
general in nature and are intended to represent major  generators of solid
wa'ste, for which collection and disposal programs must be provided.  De-
tailed present and future land use studies were conducted by the Omaha-
Council Bluffs Metropolitan Area Planning Agency and  furnished for use in
this report.  The base map used in Figure III-3  indicates the generalized land
use projections for the Study Area by 1995.  The land use patterns  shown rep-
resent the major concentrations  of residential, commerce and industry  de-
velopment which are  expected to have a measurable  effect  on the size and lo-
cation of future  solid waste disposal facilities.
D.
EXISTING SOLID WASTE FACILITIES
         1.       Name and Location.  Twenty-one major and minor disposal
facilities in the Study Area were located and surveyed.  These facilities were
selected because they received material from one or more of the following
sources:
                 a_.    Public collectors of solid waste.

                 _b.    Private collectors of solid waste.

                 £.    General public,  including the domestic,  commercial
                       and industrial segments.

Not included were strictly private disposal facilities operated for the exclusive
use of one or more industries  or commercial establishments.  These private
facilities were included in other  surveys described in Part II.

The name and location of the facilities surveyed are listed below and shown in
Figure 1-3.
                                 Douglas County
         Name

Omaha Municipal Incinerator
Douglas County Sanitary Landfill
Douglas County Tree Disposal
Omaha City Landfill
Mi Hard Dump
                                         Location

                                  601 Seward Street
                                  108 and Maple Street
                                  140 and Fort Street
                                  34th and Wood Avenue
                                  North of 156th and Harrison Street
                                   1-9

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                EXISTING
            DISPOSAL  SITES
I-IO
                    FIGURE T-3

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                            TABLE 1-1 - EXISTING LAND USE (Acres)
tit-
                                                Public &     Parks and     Total
              Residential Commercial Industrial Semi-Public Recreation  Development
Vacant    Total
Douglas County
Omaha 2 1 ,
Ralston
Millard
Boys Town
Bennington
Elkhorn
Valley
Waterloo
Total Cities 22,
Rural 20,
Total Land 43,
Total Water
Total
Sarpy County
Bellevue 1,
Papillion
La Vista
Gretna
Springfield
Offutt AFB
Capehart
Total Cities 2,
Rural
Total Land 3,
Total Water
Total Land & Water
Pottawattamie County
Council Bluffs 5,
Avoca
Cars on
Carter Lake
Crescent
Hancock
Macedonia
McClelland
Minden
Neola
Oakland
Treynor
Underwood
Walnut
Rural Non-Farm
C.B. Planning Area 2,
Total Land 9,
Total Water
Total Land & Water

939
306
372
7
64
64
152
66
970
097
067



443
398
287
127
70
_
367
692
782
474



088
227
117
420
68
43
54
41
48
98
205
70
57
129
350
524
539



3,930
15
69
--
7
7
20
8
4, 056
118
4^174



153
17
6
11
13


200
28
228



745
46
4
30
7
12
6
6
10
12
20
13
9
16
137
653
1,726



4, 948
15
116
_-
19
10
83
4
5, 195
980
6, 175



65
8
25
8
15


121
1, 770
1,891



1,245
6
7
87
--
14
4
7
2
13
18
3
2
5
287
804
2,503



6,878
102
321
678
41
97
38
29
8, 184
1,063
9, 247



214
53
211
3
7
1,907
--
2,395
1, 677
4, 072



636
20
8
152
7
4
7
1
10
8
19
6
10
4
4, 544
1, 110
6, 545



2, 730
26
26
--
1
2
7
1
2, 793
933
3, 726



72
26
19
-_
--
-_
--
117
1,455
1,572



169
29
11
--
6
129
3
2
--
3
39
78
1
--
2,012
125
2, 607



40,425
464
904
685
132
180
300
108
43, 198
23, 191
66,389



1, 947
502
548
149
105
1, 907
367
5,525
5, 712
11,237



7,883
328
147
689
88
202
74
57
70
134
301
170
79
154
7,330
5, 216
22, 920



4,375
410
2, 901
1,354
116
66
316
40
9,578
138,241
147,819



567
107
41
65
65

--
845
140,622
141,467



4,230
678
103
687
534
218
55
65
91
188
499
52
200
263
566, 398
19,267
593, 528



44,800
874
3,805
2, 039
248
246
616
148
52, 776
161, 432
214, 208
4,032
218,240

2, 514
609
589
214
170
1, 907
367
6, 370
146,334
152, 704
6, 016
158, 720

12, 113
1, 006
250
1, 376
622
420
129
122
161
322
800
222
279
417
573, 728
24,481
616,448
3,712
620, 160
                                             1-11

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                             Sarpy County
       Name

Sarpy County Sanitary Landfill
Bellevue Landfill
S & L Landfill
Papillion Dump
Cretna Dump
Springfield Dump
         Location

1 Mile West of 36th and Capehart Road
10th and Warren Street
2 Miles West of LaPlatte & Highway #73*
1 Mile West of 6th and Washington Street
3 Miles Southwest of Gretna on Highway #6
1/2 Mile Northeast of Springfield
                         Pottawattamie County
Meese Sanitary Landfill

Council Bluffs  Landfill
Council Bluffs  City Dump

Avoca Dump

Carson Dump
Plancock Dump
Macedonia Dump
Oakland Dump

Treynor Dump
Walnut Dump
1 Mile East of Mormon Bridge on Highway
  #36
3200 South 16th Avenue
1 Mile North of Council Bluffs on North
  15th Street
2 Blocks Siutheast of Chestnut and
  Ellsworth Street
1/4 Mile West of Carson  on Highway #92
2 Miles South of Hancock
1 Mile South of Macedonia on County M-21
2 Blocks South of Brown Street and
  Highway #59
1/2 Mile North of Treynor  on County L-55
3 Blocks Southeast of Walnut
         2.       Survey of Existing Facilities.  Detailed information pertaining
to each of the existing solid waste disposal facilities,  with the exception of the
Omaha  Municipal Incinerator, was compiled using Land Disposal Site Investigation
Report  forms developed by the U. S.  Public Health Service.  A  sample of this form
is included in the Appendix as Exhibit 1-1. The Omaha Municipal Incinerator,
which was once a major facility,  ceased operations during the study and was  con-
verted into a transfer station.

A recap of the survey data for each of the disposal facilities is shown in Table
1-2,  Pages 1 and 2.

The Solid Waste Training Section, Training Program, National Center for Ur-
ban and Industrial Health, Cincinnati, Ohio,  has developed a tentative rating
method for sanitary landfill operations.  (During the period this study and re-
port were conducted and after the  existing facilities were surveyed, the  rating
method was slightly changed in a few items.   The rating  method used in this re-
port is  that which was current at the time of the survey. ) This rating method
contains the essential elements to indicate the quality of  sanitation which landfills
must maintain in order to operate in three principle types of areas.  In many situ-
ations,  sanitary landfills may attain a rating appropriate for the area in which
they are located, through modifications to acquire adequate scores on specific
items.
                                      1-12

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In a sanitary landfill, the sanitary condition of the fill should be maintained
at all times; therefore, a high score must be attained and maintained on cer-
tain "must"  items in order to assure the proper degree of health protection.

A sample of the tentative rating system is reproduced in the Appendix of this
report as Exhibit 1-2.  A summation of the points awarded for  each of the twenty
seven items yields a possible score of up to 100.  The method  used for evalu-
ating the numerical ratings is as follows:

         A-Rated.  Sanitary Landfill - Suitable  for well developed areas
         such as residential and commercial zonings.  The  total rating
         must equal 85 or more points.

         B-Rated.  Sanitary Landfill - Suitable  for areas of industrial
         zonings. The total rating must  equal 70 or more points.

         C-Rated.  Sanitary Landfill - Suitable  for remote or rural areas.
         The total rating must equal 55 or more points.

The following items of the tentative  rating form must score as  indicated in or-
der to qualify for any of the three ratings listed.  These items  are referred
to as "must" items.

         Must Items                      A-Rated   B-Rated   C-Rated
Item  9     Blowing Litter                   422
Item 12     Daily Cover                     15        10         10
Item 13     Intermediate Cover               311
Item 14     Final Cover                      333
Item 18     Burning                          331
Item 22     Placement of Ground Water       533
Item 23     Drainage of Surface Water        6         -          -

Of the twenty (20) major and minor disposal facilities investigated throughout
the Study Area, only six (6) had the potential of being called sanitary landfills.
Most of the remaining fourteen (14) disposal facilities are entirely inadequate
and can be described as open, uncontrolled, burning dumps,  since they do not
comply with sanitary landfill standards,  nor can they qualify for the minimum
C-rating of 55 points or more.

The "must" items with which a sanitary  landfill must comply have been listed
and rated for each landfill operating in the Study Area and are shown in Table
I- 3 of this  report.  Of the six landfills listed, three were rated  as sanitary
landfills; Douglas County SLF, Sarpy County SLF and Meese SLF.
                                  1-15

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A brief summary of the existing landfills listed in Table 1-3 is included in the
following paragraphs.

The Douglas County Sanitary Landfill received a total of 79 points for all
items listed on the sanitary landfill rating form and qualified  for a B-rating,
suitable for an area of industrial zoning.  Improvement in "must" Item #9,
"Blowing Litter", along with improvements in several minor  items listed on    *
the sanitary landfill form (access road,  etc. ) would qualify this site for an
"A-rated" sanitary landfill.

The Sarpy County Sanitary Landfill received a total of 79 points for all items
listed on the rating form and qualified for a B-rating,  suitable for an area of
industrial zoning.  (Since the time the ratings were made this site has begun
a program of controlled burning of tree  waste.  Under the new rating system,
any deliberate burning, regardless of the degree  of control, would disqualify
a site from receiving any "sanitary"  rating. ) Improvement in "must" Item
,'/9, "Blowing Litter",  along with other minor improvements would qualify this
.site for an "A-rated" sanitary landfill.

The Meese Sanitary Landfill received a  total of 87 points for all items listed
on the  sanitary landfill rating form which is more than enough for an  "A"
rating;  however, due to "must" Items #9 "Blowing Litter" and #22 "Placement-
in Ground Water" which were rated "B", this site must be given a "B"  rating,
suitable for an industrial zoning.

The Bc-tlevue and S & L Landfills  each received 53 total pomts for all items
listed on the sanitary landfill rating form but could not be rated as  sanitary
landfills since both sites deviate  materially from "must" Items #9 "Blowing
Litter" and #18 "Burning".  Improvements siich as fencing to control blowing
litter and prohibiting open burning are needed,  along with other minor site
improvements in order to upgrade these sites into C-rated sanitary landfills
suitable for rural areas.

The Council Bluffs Landfill received 46  total points for all items listed on
the sanitary landfill rating form and could not be  rated as a sanitary landfill since
this site lacks adequate points and deviates materially from "must" Items #9
"Blowing Litter, " and #12 "Daily Cover", and #13 "Intermediate Cover" to
qualify  for the minimum C-rating of 55 points or  more.   This landfill is entirely
inadequate since sufficient cover material is not available to  cover refuse and
intermittent contact occurs between refuse and groundwater table.  This site
does not comply with the essential "must" items to indicate the quality of sani-
tation which sanitary landfills must maintain.
                                   1-16

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Tin;  ratings which were assigned could vary from day to day and from week
to week.  Generally,  the  ratings assigned were those observed during the
site  survey except where there were reasons to believe the conditions at that
time were unusual.  In which case,  other observations were made at other
times   These ratings are not official in any way and are included in this re-
port solely for the purpose of indicating the general condition of disposal facili-
ties  in the Study Area.                                                          *

To insure that the appropriate standards, regulations, and laws  for the proper
operation of a sanitary landfill are complied with, a sanitary landfill site and
operation should be inspected at least once a  month by the Health Officer, or
other public official charged with  this responsibility, in whose jurisdiction of
the facility is located.

Although the U S  P. H. S  recognizes the Types B i
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 Because garbage collection is an unpopular subject,  many governmental units
 give this area little attention.  The sanitation departments of many municipali-
 ties are operated by senior garbage collectors who have come up through the
 Banks; although they understand how the garbage cans are to be emptied and trucks
 are driven, they lack  even the fundamental managerial skills necessary to proper-
 ly spend a large portion of the municipal tax  dollar.  They are unacquainted with
 ftscal and personnel management procedures and modern engineering techniques.

 When compared to  other services and utilities, the cost of collection and dis-
 posal of solid waste is not high.  Figure 1-4 shows the approximate annual cost
 per dwelling unit of several common services and utilities.  Although the cost
 per dwelling unit is not great,  it still represents a major item in a municipal
 budget, usually ranking fourth after schools,  streets and police  and fire protect-
 ion.

 Unfortunately,  even when  spending too much  for benefits received,  the level of
 service and operating  techniques are frequently inadequate, antiquated and un-
 sanitary.  Improved management can usually improve  service and reduce cost.

 Civic leaders,  both professional and lay, are often uninformed about solid
waste management. If the level of knowledge can be raised in government con-
 cerning these matters, tax dollars can be saved,  services expanded, and sani-
tary conditions improved.   The tax savings and expanded services are important
and desirable,  but the improvement in sanitary conditions  is mandatory if the
public  safety and welfare are to be preserved.

Improving  sanitary conditions through proper solid waste management should be
approached in two ways.  First,  there must be laws  which establish minimum
 standards of practice plus  effective enforcement;  and secondly,  there must be a
program of public information showing how solid waste management can be econ-
omically pursued.

Solid waste storage, collection, transportation and disposal must be  managed as
a vital link in the control of water, air and land pollution.
                                   1-19

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      A.  COLLECTION  a  DISPOSAL  OF  SOLID WASTES
      B.  SEWER SERVICE (WASTE WATER  TREATMENT)
      C.  WATER
      D.  GAS
      E.  ELECTRICAL  POWER
      F.  TELEPHONE
      G.  TELEPHONE  EXTENSION
         COMPARING  SOLID WASTE  COLLECTION
                   & DISPOSAL  COST  WITH
                OTHER  SERVICES  a  UTILITIES
                         1-20
                                                 FIGURE  1-4

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J\	PRESENT TECHNOLOGY

         !.       General.  The technology to collect,  transport and dispose
j.)f solid waste is available for immediate use.  New techniques are under in-
vestigation and much research and development is being done.  Hopefully,
some of this work will produce better methods, lower  costs and refinements to
Existing methods.  We can also hope that,  eventually,  processes will be devel-
oped which can economically convert our present wastes  into useful products
to be recycled in  the economy.

For the present,  the monumental task that must be accomplished is the improve-
ment of many of our existing systems,  from their present antiquated  status through
the use of  modern technology which is currently available.

         2,       Collection Systems.   Solid waste collection is a responsibility
of the public, along with water supply,  sewage disposal,  streets, fire and police
protection.  These services are usually provided by local government, and paid
for through taxation or a service charge.  It is recognized that a government  can
provide these necessary services  for the public more efficiently and economically
than the individual can provide them for himself.   Further and specifically in the
case of collecting solid waste,  if the local governmental unit does not  provide for
collection  services, many citizens do not adequately provide for their own waste
disposal.  As a result, the entire  community suffers.

There are  three basic types of collection service, ie.  Municipal, Contract and
Private.

                  ja.    Municipal  and Contract Systems.   The municipal and con-
tract systems are similar.  Both are under the control of the municipality. They
operate on established routes  serving the entire residential  areas on a scheduled
basis.  Under these systems the community receives regular collection of its
domestic waste.   The system  is planned,  organized and supervised by the muni-
cipal government. The results are an efficient collection service at a reasonable
cost to the community.

The basic difference between the two systems is  that the  municipal system operates
the service using  Its  own manpower, equipment and facilities, whereas the contract
system  uses the manpower,  equipment  and facilities of a private contractor to op-
erate the system under an agreement between the contractor and the municipality.

The municipality capable of  operating its own system efficiently,  usually has  a
lower unit  collection  cost than the community contracting with private haulers.
The municipality can operate the system without  a required  profit whereas the
private  contractor cannot.  There  are other  cost factors  in favor of a  system
owned and  operated by a municipal government.  Tax savings in the purchase  of
equipment  and supplies and in the operational cost of equipment lower collection
costs.  A municipally controlled collection system, properly planned and
                                       1-21

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supervised, will provide satisfactory service to the public,  whether the system
is municipally owned or contracted with a private hauler.  The cost to the public
is the  principal consideration.

                  b.    Private System. With a private  system the municipality
has a minimum involvement with the collection of waste, usually limited to con-
trolling ordinances and the licensing or franchising of collectors.  Some commu-
nities  do not require any of these items.  Private collectors contract directly
with the property owner for an agreed fee.

When collections are left entirely to an agreement between the property owner
and the private hauler, the service is generally not as efficient as  the other sys-
tems.  The private system places the responsibility for  the collection of waste
with the individual property owner who  may, or may not have a conscientious
concern for the problem.  Usually several private haulers will compete within a
community to provide service.  This  competition will tend to keep  the charges
uniform; however, it will prevent any one private collector from establishing
an efficient route where he can collect  from all property owners in a given area.
As a result,  the  cost to the individual is usually higher  than either the municipal
or the contract system.

For  small communities,  the  operation  of a municipal system may  not be econ-
omical if  only  the one community is involved,  but  several communities may
find  it economically feasible to join together to operate  a municipal type system
as a cooperative venture under the  existing authority and as  proposed in
recommended  legislation.

Collection systems may collect only domestic  waste or  may, if desirable,  collect
domestic,  commercial and industrial •wastes,  or a combination of  the several.
Frequently municipalities include many commercial establishments in their col-
lection systems, particularly where the waste from these establishments are not
large in volume or difficult to handle.   This is  done as a convenience and may
result in a savings to the establishment.  Many industrial and some commercial
waste producers require special  service which a municipality may be unwilling
to provide. For this reason most industrial and many commercial establishments
either provide  their own removal service or engage the  services of a private  sys-
tem.  There is no  technical or financial reason why this service could  not also be
provided by a municipal system.  Each  case should be considered on its own
merits.  Table 1-4 shows the type of collection system currently being used
in the various  communities in the Study Area.

A variety  of specialized equipment is available for collection of waste.  The most
common item  is the packer truck, which also  comes in a variety of sizes and
arrangements.  Basically, this  is a totally enclosed and watertight body mounted
on a truck chassis.   It has a device which compacts the loose solid waste into a
                                    1-22

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 smaller volume, enabling the truck to carry more material than it could Jf
 placed in 'he body  in a loose condition.  Many packer trucks can carry three  or
 more  limes  as much material as a non-packer truck of the same size.   The
"advantages of such a truck are particularly significant when long hauls to a disposal
 site are required.  In addition to the  economy, the truck is totally  enclosed and
^watertight, providing a significant reduction in litter.

 Containers of various types are also  available.   Some are designed to be left at
 a customer's premises and when filled are exchanged for an empty container.
 The filled container is removed to a disposal facility where it is emptied and avail-
 able for reuse.   Some containers are designed to be left  at a customer's premises
 and when filled are simply emptied into a type of packer  truck.  After emptying
 several or many containers, the truck is driven  to a disposal site for emptying.

 The train system is available.   This  system employs a series.of relatively small
 trailer units pulled by a light-weight  truck, along a collection route.   From time
 to time a packer truck fitted with a lifting device, is dispatched to  meet the train
 system.  The packer truck lifts each trailer and contents,  one at a time, and
 dumps the contents into the truck.  The train then continues collection and  (he pack-
 er truck may either proceed to other train crews or when filled, proceed to the
 disposal site.

 Packer trucks,  containers,  trains  and other  systems or devices are available in
 a variety of  sizes,  shapes and functional arrangements.  The best  system, size,
 shape  or arrangement depend on many local  factors and must be determined after
 a careful study.  This  equipment is available from many manufacturers. The
 proper application  of the proper equipment,  together with a carefully planned
 and operated system,  can be very  beneficial to a community.  A first rate sys-
 tem frequently is less  expensive to a community, when the total cost to  a community-
 is considered, than a  poor system or no system at all.

         3.       Transportation Systems.  Solid waste,  when collected, must
be transported to a place of final disposal.  This  is usually accomplished in
 the vehicle in which it was collected but it may be transferred to a special haul-
ing vehicle suitable for this purpose.

Direct hauling in a collection vehicle  presents no special problems and is the most
 straight forward way of accomplishing the task.   There are,  however, many  fac-
tors which must be considered,  including in  part; the haul distance,  in  both
time and miles; the lost time for crew members, who are not productive when
their collection vehicle is hauling;  and the size of the  pay load for hauling pur-
poses  vs. the desirable size of the vehicle while  on route.   These factors must
be weighed against the alternative of transferring the  collected load to a special
hauling vehicle.
                                    1-23

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             TABLE 1-4 -INVENTORY OF COLLECTION PRACTICE
DOUJJLas County
Bennington
Boys Town
Elk City
Elkhorn
Irvington
System

Private
Private
Private
Private
Private
  City

Millar d
Omaha
Ralston
Valley
Waterloo
   System

Private
Muni-Contr.
Muni-Contr.
Private
Private
Sarpy County

Bellevue
Chalco
Or etna
LaPlatte
La Vista
Private
Private
Private
Private
Private
Meadow
Me Ha
Offutt
Pa pillion
Springfield
Private
Private
Contract
Private
Private
Pottawattamie County

Avoca                 Private
Bentley                Private
Carson                Private
Carter Lake           Private
Council Bluffs          Municipal
Crescent              Private
Dumfries              Private
Hancock               Private
Honey Creek           Private
Loveland              Private
                 Macedonia
                 McClelland
                 Minden
                 Neola
                 Oakland
                 Quick
                 Treynor
                 Underwood
                 Walnut
                 Weston
                   Private
                   Private
                   Private
                   Private
                   Private
                   Private
                   Private
                   Private
                   Private
                   Private
The most common form of special hauling is the Transfer Station.  A transfer
station is a facility, usually centrally located,  which is equipped to efficiently
receive various loads of waste from collection vehicles or other vehicles and
place them in large semi-trailers for hauling to a place of disposal.  To be
economical,  it is  necessary that the cost of transfer and haul must be  less than
the cost of direct  haul.  Only a careful study of the exact local conditions can
determine when a transfer station should be provided.
                                  1-24

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The knowledge of how to design and operate transfer stations, and all of the
necessary equipment is available.

Other forms of transfer or transportation are available  or are under study.
Some communities use barges while others are using or are planning to use
railroad facilities.  Studies are  under way to investigate the transportation of
solid waste in slurry form in pipe lines and in  dry form in vacuum pipes.  All
of these systems are special conditions which may be considered on their own
merit.

         4.       Disposal Systems.  Solid waste  disposal can be accomplished
using any of several methods.  The selection of the  most appropriate method
depends on the particular  circumstances that prevail at  the time and in the loca-
tion where the disposal is needed.

The old town dump,  where refuse was burned from time to time was once ac-
ceptable when there were  fewer  people, less intense land development and lit-
tle knowledge of air and land pollution. Today this practice is inappropriate.

In some seacoast communities combustible refuse is burned on barges far out  to
sea and the residue dumped into the water.   This  practice is now condemned as
a source of air and water  pollution.

In the large metropolitan regions such as the New York  City area, land, labor
and transportation costs present a different set of circumstances than prevail in
the Omaha-Council Bluffs Metropolitan Area.  Each community or region must
consider methods which are based on local conditions.

In the following paragraphs, three basic processes for disposal are discussed:
Incineration and landfilling, composting and  landfilling,  and sanitary landfilling.

                  a..    Incineration and Landfilling.  This process  consists of
two parts;  ie. the reduction of volume of combustible materials through the use
of an incinerator; and the  landfilling of incombustible waste and incinerator resi-
due.  Much of the total •waste of a community is incombustible and is normally
disposed of in a sanitary landfill or some other land disposal process.   The com-
bustible waste can be significantly reduced in volume in an incinerator.  The
residue or ash which remains after incineration can be disposed of in sanitary
landfills.   The incineration process consists of reducing combustible solid waste
to an inert residue by burning, within an enclosure,  under high temperatures and
controlled  conditions.  When accomplished in a large facility for a community
with waste transported to the facility from several sources it is referred to as
Central Incineration.  When accomplished by individuals or commercial,  industrial
or institutional concerns for their own locally generated waste is referred to as
On Site Incineration.
                                   1-25

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Central and On Site Incinerators are used for two purposes; to reduce large
volumes of waste to a small volume of residue and to change the form of a
material which may be dangerous or a nuisance  to one which is safe or nuisance
free.

Municipal incineration plants are familiar to the general public.  Unfortunately
many poor examples are in existence today.  They should not be considered as
typical of what a modern plant can be. The modern  plant with proper air pollu-
tion control devices, burning at high temperatures and equipped with proper
controls and site facilities can be operated in any area zoned for industrial use
without creating a nuisance.

There are some incinerators in the United States which are fine examples  of in-
dustrial architecture.  Much of the public would be unaware  of the function of the
facility if it were not for signs on the building or at the gates.

A major advantage of the central incinerator is the relatively small land require-
ment and the ability to locate the plant in an industrial area within a city.  The cen-
tral location reduces the hauling cost not  only for the city collection crews, but
also for the industrial and commercial users of the facility.   This advantage is par-
ticularly important in large  metropolitan  areas where there  is a high  cost  in
hauling materials from the place where the waste is generated,  to landfill  sites
in rural areas.  It is not as  important in any location where  rural land is available
within a few minutes driving time from the center of the  City.

It was found that in this metropolitan area under the present circumstances,  in-
cineration is not practical due to reasonably close potential landfill sites.

The major disadvantage is the cost of initial construction and the cost of main-
tenance and operation. These costs usually range upward from $7.00 per ton of
waste delivered.

Modern incinerators generate considerable amounts of •waste heat.  In some  new
plants heat is now being put to economical use as steam which is either used for
generation of electricity or used directly  as steam or hot water in a variety of
processes.  The steam or electricity thus produced is sold to offset part of the
cost of operation.  The first cost is higher but frequentlyit is a worthwhile in-
vestment.

Formerly excess air was introduced into  incinerators to reduce the temperature
of the stack gases.   With increasing air pollution requirements the cost of scrub-
bing these excess air quantities is greatly increased.  The recovery of excess
heat in the form of steam not only produces a valuable by-product, but also re-
duces the required quantity of excess air  which  in turn reduces the cost of scrub-
bing the stack gases.
                                 1-26

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Certain industries,  commercial establishments and institutions may wish
to operate on-site incinerators as a matter of convenience.  If they are
properly designed and operated they should be permitted.  The design, how-
ever, must include all of Ihe necessary controls and devices to insure pro-
per burning and safety and air pollution controls.
 •
Some on-site incinerators may be necessary.  For example, the  safe disposal
of infectious or otherwise contaminated materials fromhospitals  or drug man-
ufacturers requires incineration.  Also highly volatile and inflammable liquids
from other industries cannot be safely buried in a landfill.  In these cases, in-
cineration is necessary  and an acceptable method of disposal;  however, they
should be licensed and controlled.

In the event a community or industry would find it to their advantage to construct
and operate an incineration facility, the technology and equipment is available
to accomplish the task without pollution to the water, air and land of the com-
munity.

                 Ib.    Composting and Landfilling.  This process consists of
two points; ie. the conversion of the organic portion of solid waste to compost
referred to as "composting"; and the landfilling of the non-compostable material.
Composting is the conversion of the organic portion of the solid waste through
aerobic digestion, to a stable and harmless material, which may be used for a
soil  conditioner.

Micro-organisms which are present in garbage  and other  organic material will
cause the waste to decompose.  The composting plant provides the proper  en-
vironment for these organisms.   The  plant receives only those loads  of solid waste
which can be composted.  Loads not suitable for composting are diverted to sani-
tary landfills.  The waste which is accepted is  picked to remove additional non-
compostable materials.   Some of these materials have a value and are salvaged.
After picking, the remaining material is pulverized and moisturized with vari-
ous processing equipment.  The material is then subjected to a composting  period
varying from one to two weeks during which time the temperature, moisture and
air content is carefully controlled,  and the material is periodically mixed.  At
the end of the composting period, the waste has been converted to compost, a
humus like material having some value as a  soil conditioner.

Composting has been practiced for many years with little  success.  In recent
years, several research and development projects have been undertaken-which
have improved the  process.  The modern plant  of today is a highly mechanized
facility utilizing quality equipment designed or  specifically adapted for this process.
Several well known national companies and equipment manufacturers have built
and are or were operating compositing plants in Texas, Arizona,  Florida and
elsewhere.

                                1-27

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Unfortunately,  some of these modern plants have had serious difficulty with
odor problems.  It is assumed that these problems can be overcome and with-
in a few years  it will be possible to process compost in a nuisance free  man-
ner.

The cost of compositing Is considerably greater than the cost of landfilling.      ^
One recent plant constructed by a national company in cooperation with a major
Florida City was placed into operation and received 100 tons of compostable
refuse per day.  The City pays a fee of approximately $3. 25 per ton to the op-
erator to take the material.  This fee is more than 2 times the  cost of landfill-
ing and in addition the non-compostable material must be landfilled.

Whether the compost material can be sold  is  a debatable question.  Attempts
to sell soil conditioners in large quantity have not been successful.  In the event
the material cannot be  sold, it must also be landfilled.

It is possible that the composting processes may be practical some years in the
future.  Today, in the Study Area, it is not recommended as a satisfactory
method of solid waste  disposal.

                 .£•    Sanitary Landfilling is a process in which solid waste
materials are spread on the ground,  crushed and compacted into a dense mass and
covered with earth in a carefully controlled sanitary manner.  This method is a
proven system which when carefully planned and operated is economical,  nuisance
free,  and does not pollute the water, air  or land.

The filling can be on land ranging from level land to gullies or ravines.   In many
instances,  rough and low value land has been improved by filling.

The term  sanitary landfill has frequently been confused with open dumps or burn-
ing grounds.  This is incorrect.   A sanitary landfill is a  specific process  requiring
careful design  and management, proper equipment and operating techniques to
assure that sanitary conditions are maintained at all times.  The compacted waste
is completely  covered with earth on a daily  schedule.  Each day's waste  is there-
fore enclosed in an earth cell.  These cells preclude rodents  and insects,  odors,
litter, air and water pollution and fires.  Emphasis is placed on proper  location,
equipment,  compaction and cover, sight  screening,  landscaping and other  sani-
tary and aesthetic requirements.

The major disadvantage is that relatively large quantities of land are required.
In certain parts of the country this requirement can be disqualifying.  In the
Study Area, adequate land is available at locations within economic hauling dis-
tances.
                                 1-28

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Another potential disadvantage is the frequent lack of public acceptance of
sanitary landfilling.  This is due to the bad reputation of dumps and the pub-
lic, confusion of dumps and sanitary landfills. A good public relation program
and" a demonstration of proper sanitary landfill operations can reduce the pub-
lic resistance.

Kxcept for very small or unusual operations, most sanitary landfills can be
owned and operated for approximately $1. 40 per ton.  When compared to the
cost of incineration and composting this method is usually the least expensive.

Several variations of the sanitary landfill method are frequently used.
Certain materials  such as broken concrete,  demolition waste, ashes, etc.
can be used to fill  gullies, worked out quarries  or low land without requiring
fuJl sanitary landfill methods.  Filling a dry area with such material is re-
ferred to as dry landfilling.   Filling areas which could be wet from ground
water or surface overflow with suitable material is  referred to as wet land-
filling.

The sanitary landfill method is recommended for the Study Area for the
following reasons:

       (1)     Land is  available.

       (2)     The method has been proven satisfactory where properly
               operated.

       (3)     The method can meet all health,  sanitation and pollution
               requirements,  and be aesthetically pleasing.

       (4)     The method is adaptable to varying quantities and peak or
               slack rates.

       (5)     The method is the most economical.

The technology and equipment for sanitary landfilling and variations of the
system are now available.  The  process is reasonably simple  and economical,
but it is not sufficiently simple that it can be designed and managed without
attention by knowledgeable people and it cannot be done without adequate  funds.
Landfiiling should be designed by engineers and managed by  competent
authority.  It must also receive  the necessary funds to be operated properly.
                                 1-29

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                PART TWO - SURVEY OF SOLID WASTE

 A^	GENERAL .  This part of the report contains an analysis of the
 present and future quantities and characteristics of the solid wastes  generated
 within the Study Area.

 The survey of solid waste materials was made in two parts.   The first part
 was concerned with those materials which were  being disposed of at  major
 public disposal facilities.  Extensive site surveillances were  conducted at
 seven major public disposal facilities and are described in Section E.

 The second part was concerned with those materials which were being dis-
 posed of at other than public  disposal sites,  referred to as "On Site" disposal.
 The on-site disposal includes those materials which can be expected at public
 disposal sites in the future and those materials which will  continue to be dis-
 posed of and/or accumulated on site.  The on-site materials were  compiled
 from commercial and industrial surveys described in Section B and through
 special studies which were conducted to evaluate the wastes from scrapped
 automobiles,  diseased trees,  packinghouses and commercial  feedlots.  These
 studies are described in Section D.

_EL	COMMERCIAL AND INDUSTRIAL SURVEYS

         1.     Surveys .  A survey was conducted to determine  the nature
 and magnitude of wastes from various commercial and industrial firms in
 the Study Area.  The purpose of this  survey was to determine if there were
 individual companies or types of companies with wastes that could have a
 significant effect on disposal practice.   In addition, the survey provided data
 which could be used to supplement waste quantity information  obtained from
 the landfill study such as present and future  material which can be  expected
 at a public disposal after air pollution control and stricter landfilling regula-
 tions have been put into effect. The firms surveyed were selected  from a
 complete listing of industrial and commercial firms in the  Study  Area.

 A  personal visit or telephone call  was used to secure  detailed information
 from 95 firms, representing construction; manufacturing;  transportation
 and public utilities; wholesale and retail trade; finance, insurance and real
 estate;  and services.  Information pertaining to the nature  and quantity of
 waste,  and information concerning those wastes  which are  considered
 hazardous, contaminated or otherwise requiring special handling in trans-
 fer and disposal operations was gathered. Liquid wastes such as oils, sol-
 vents, paints  and inks which cannot be discharged to the sewer system are
 included in this category.

 All of the firms interviewed were  evaluated as to type of process or product,
 nature of the waste, general magnitude of waste  and method of disposal.
                                   II-1

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         2.      Waste Quantity. The firms contacted were categorized as
to type of business activity and divided into general type of product or process
for evaluating the quantities of waste generated.  The categories of waste are
listed in Table II-1

Quantities of waste were estimated in most cases by plant superintendents ,or
office managers.  Most  of the estimates were in terms of daily or weekly
volumes with some weight information to assist in  determining bulk densi-
ties for the  various categories.  The reliability of  the estimates  varied con-
siderably due to the fact that the smaller establishments generally estimated
in terms of  number and  size of storage containers,  while in larger firms,
particularly manufacturers, the magnitude  of the waste  disposal  operation,
and production accounting procedures necessitated more specific knowledge
of quantities involved.

In order to  establish a basis for relating the data obtained from the survey
to the total  waste generated in the  Study Area, waste quantities were  evalu-
ated in terms of the number of employees in the  individual firms contacted.

Table II-l lists each of the  individual categories  in the commercial and in-
dustrial  survey and shows the maximum, minimum and  average waste quan-
tity generated per employee per day.  Quantity figures in terms of average
daily pounds per employee  are based on a full 7-day week.  Suitable adjust-
ments were made to reflect actual quantities when  the work week was less
than 7 days.

         3.      Total Industrial -  Commercial Waste.  The present  indus-
trial and commercial wastes were projected using  the data obtained from the
survey.  The employment statistics used were from the 1967 County  business
patterns. Projections were made  for each of the categories listed in the
preceding paragraph.  Table II-2 shows the estimated present quantities  of
waste in both cubic yards per day  and tons per day, and gives the percentage
surveyed of the total employment in each category.  Approximately 25%  of
the total employment of  the manufacturing group was surveyed,  and approxi-
mately 21%  of all groups of the total non-agricultural employment in  the
Metropolitan area were  included in the  survey.   The quantity data is  summa-
rized in  Table II-3.

In order to  establish the amount of present and revised  public site disposal
and on-site  disposal, the quantities in Table II-2 have been tabulated as
follows:

                1.    Present quantities of waste material currently
                      being sent to public disposal facilities.

                2.    Present quantities of waste material currently
                      being disposed of on-site or  accumulated on-site.

                                    II-2

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        TABLE II- 1.  COMMERCIAL AND INDUSTRIAL SURVEY
MATERIAL QUANTITIES PER EMPLOYER



NO. OF

FIRMS
CATEGORY SURVEYED
I.


II.
















III.

IV.









V









VI.

VII.


Construction
A. Demolition
B General Contracting
Manufacturing
A. Food and Meat Products
B. Grain Mill Products
C Apparel and Related
Products
D. Lumber and Wood
Products
E. Paper and Allied Products
and Printing and
Publishing
F. Chemicals and Allied
Products
G. Stone, Clay and Glass
Products
H. Primary Metal Industries
I. Fabricated Metal Products
J. Machinery
Transportation and Other
Public Utilities
Wholesale Trade
A. Motor Vehicles and
Automotive Equipment
B. Drugs, Chemicals, and
Allied Products
C. Groceries and Related
Products
D. Electrical, Machinery and
Hardware Goods
E. Miscellaneous Wholesales
Retail Trade
A Building Materials and
Farm Equipment
B. General Merchandise
C. Food
D. Automotive Dealers
E. Apparel and Accessories
F. Furniture and Home
Furnishings
G Miscellaneous Retail Stores
Finance, Insurance, and
Real Estate
Services
A. Amusements
B. Miscellaneous Repair

4
14

7
3

2

3
3


3

8

2
2
3

6

8

3

2

5

3

2

2
2
3
4

3
2

3

3
5
RANGE
LB/EMP/DAY
MIN/MAX

2000/14,800
3. 0/111.0

2.2/13.8
15. 1/35.0

1. 1/4,4

10. 7/35. 0
2.4/40. 0


1. 1/83. 1

5. 7/266. 7

5.9/127.3
2. 7/7. 0
4.8/17. 1

0.2/111.3

12/360

4. 7/10. 0

3.4/6.5

0. 5/5. 6

0. 7/120. 0

2. 1/7. 1

1.2/1. 5
21. 1/44. 0
2. 0/43. 1
1. 0/10. 0

15. 5/263. 6
6.7/11. 1

0.9/6.9

7.4/17. 1
0.9/2. 9

AVG
LB/EMP/DAY

4000
5.0

13.8
17.3

3. 7

26. 1
4. 1


37. 1

143.0

68.8
6.8
5. 1

73.0

186

6.2

4.9

2. 7

17

4.6

1. 3
37.2
27.2
2. 1

68.3
8. 7

1. 1

11.5
1.4
        Services
C.  Hospitals and Medical
        Services
1. 7/3. 4
2.
                                II-3

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                           TABLE II-Z.   COMMERCIAL b INDUSTRIAL SURVEY - MATERIAL QUANTITIES


I

II








III

IV





V






VI.

VII




VIII,
IX


CONSTRUCTION
B General Contracting
Total
MANUFACTURING
B Grain Mill Products
C Apparel & Related Products
D Lumber fe Wood Products




J Machinery
TRANSPORTATION t PUBLIC UTILITIES
Total
WHOLESALE TRADE
B Drugs, Chemicals & Allied Proc
C Groceries & Related
D Electrical & Hdwe Goods
E Machny, Equip, fc Misc Whale.
Total
RETAIL TRADE

C Food

F Furniture fc Home Furnishings
G Misc Retail Stores
Total
FINANCE, INSURANCE b REAL ESTATE

SERVICES.
A Amusement.
B Misc Repair fc Auto Rental
C Hospitals
Total
C t I SURVEY DAILY
C t I SURVEY ANNUAL

Surveyed

50 0
4 1

37
69 3
22 4




48 6

50, 0

3 4
40
2 2
7. 1



2 4

17 4
1 4




10.9
6.9
27.4






1, 129
10, 159
11,288

1,375
965
375




2,835

16,364

676
1, 563
4, 787
3,984
12,597


4,596

1,229
3,299
23,511



1,407
1, 392
15,004
17,803



CY/D

2 0
114,6
116 6

116.2
7 8
31,3




79 6

53 6

17 6
40,3
81 8
260, 6
1082,8


250,0-

433.9
171 4
1060 4



64 2
10,1
96 0
170 3

1.452.335

Tons/D

2
12 9
13 1

11.9
1 7
4.9




7 3

3 2

2. 1
3.8
6.4
33 8
193 7


22.9

39 7
14.3
146 7



7. 3
1.0
13. 1
21.4

223.745

CY/D Tons/D CY/D

1683 2 2058 0 2.0
46 3 3.0 161 0
1729. 5 2061 0 163 0

116.2
2.2 14 10 0
.08 001 31 4




79 6

1260 594 2 53 6

17 6
40 3
81 8
260 6
1082 8


658. 3 62. 5 90S 3

21 8 23 455 7
171.4
680 1 64.8 1740 5



8.3 .7 72 5
10.1
74.8 6.9 96 0
83. 1 7. 6 178. 6

L 387. 365 1.012,145 L 725. 720
al to Material to
Tons/D CY/D Tons/D

2 1683 2 2058 0
15 8
16 0 1683 2 2058 0

95 5
11 9
18
4.9




73

3 2 1260 0 594 2

21
38
64
33 8
193 7


85 4

42 0
14 3
211 5



81
10
13 1 74 8 69
22 2 74 8 69

249.295 L 113. 980 986.595
Public
CY/D Tons/D
,
46 3 30
46 3 30


22 14
08 001




"

-

._
..
..

..


658 3 62 5

21 8 23
"
680.1 64 8



83 7
"
"
83 7


NOTE-  Cubic yards are loose volume as stored on premises
                                                           II-4

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                3.    Revised quantities of waste material to public
                      disposal facilities.   (This is based on current
                      quantities but reflects the intention of the firm
                      if stricter disposal laws were enacted and enforced)

                4.    Revised quantities of waste materials to be disposed
                      of on-site or accumulated on-site.  (These quanti-
                      ties are also based on current rates  but are adjusted
                      to reflect the change in disposal method mentioned
                      in 3 above.)

                5.    Additional material to public disposal.  (Based on
                      current rate  of disposal but reflects  changes con-
                      templated in  3. and 4. above.
            TABLE II-3.  SUMMARY OF COMMERCIAL AND
                          INDUSTRIAL ANNUAL WASTE QUANTITIES

                          Present (1968)    Revised (1968)	Change  _
                       Tons^     C. Y. *   Tons       C Y. * Tons    C. Y. *
         On Site    1,012,145 1,387,365  986,5951,113,980-25,500-273,385
         Public      223,745 1,452,335  249,2951,725,720+25,500+273,385
         Total     1,235,890 2,839,7001,235,8902,839,700

         On-Site      81 9%      48.9%     79-8%   39-2%    - 2.52% -19.7%
         Public       18.1%      51.1%     20.2%   60.8%    +11.3%  +18.8%

           * C. Y.  are not compacted (These C. Y. were very loose and
             should not be compared to other C. Y. ,  loose  or compacted).


The present total commercial and industrial wastes being disposed of at public
sites,  as developed in the commercial and industrial survey, is 223, 745 tons
per year as shown  in Table II-3.   This quantity is greater than  the 197,000
annual tons developed during  the landfill surveys described in Section E and
shown in Table 11-24.  The landfill survey is considered a more reliable
estimate since it is based on  a actual measurement of waste volumes  over
a week's operation at each of the  major public  landfills.  The higher values
determined from the commercial-industrial survey may be due to a number
of factors, including a tendency for the firms  to over-estimate  their quantity
of waste, a relatively large base  from which to project quantities in  some
categories, and possible  inaccuracies in projecting waste quantities  based on
employment for categories such as the meatpacking and demolition industries
which process their wastes by other internal disposal processes.
                                   II-5

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 Although a close correlation could not be made between the two surveys,
 the commercial-industrial survey did  .meet a primary objective  of estab-
 lishing an estimate of what portion of the present commercial and industrial
 wuate currently being disposed  of on-site would be diverted to public facili-
 ties if stricter landfill regulations and  air pollution controls were established
 and enforced.

 Table II-3 shows that 81. 9%  of the tonnage  and 48.9% of the cubic yards of
 the total commercial and industrial waste was disposed of in  on-site  facili-
 ties, whereas 18. 1% of the tonnage and  51. 1% of the cubic yards  were sent
 to public facilities for disposal.  The commercial and industrial  firms inter-
 viewed indicated that if stronger landfill regulations and air pollution controls
 were in effect during 1968, the  waste disposal practice would be  slightly
 different   Under these  new conditions  referred to as "revised" in Table II-2
 and Table II-3, the on-site disposal would have  been 79. 8% of tonnage and
 39.2% of the volume. The public facilities would receive 20.2% and 60.8%
 respectively.  The difference between the present and future  practice amounts
 to approximately 25, 500 tons and 273,385 cubic yards increase in public dis-
 posal and  an equal decrease  in on-site  disposal.  This  potential increase in
 materials  sent to public sites is equal to 11. 3% of the tonnage and 18. 8% of
 the volume currently being sent to public sites.  These two percentages were
 used to adjust the quantities  of commercial and industrial materials as
 measured during the landfill surveillances  described in Section B.

 The quantities of commercial and industrial waste  being disposed of on-site
 in private  facilities is very large and on a tonnage  basis is approximately
 equal to Ihe total of all waste disposed  of at public  facilities.   Some of the
 private landfills are reasonably well run and some are entirely inadequate .
 Suggested  standards and controls are recommended in  Part IV.   These faci-
 lities should be permitted  and encouraged but should be regulated to the extent
 that they do not become a nuisance or source of pollution.

_C	RESIDENTIAL SURVEY.  Residential solid waste  management con-
 sists of removing the waste from the premises for disposal at some central
 disposal facility or disposal  on-site or some combination of removal and
 on-site disposal.   In the larger communities of Bellevue,  Council Bluffs,
 Offutt AFB, Omaha and Ralston the governing body provides a regular collec-
 tion service for residential waste for its citizens.  The other municipalities
 in the Study Area do not offer this service.  A  summary of collection practice
 is shown in Table 1-4 found in Part I.

 In Bellevue, Offutt AFB, Omaha and Ralston the collection service provided
 includes all residential  waste, whereas in Council Bluffs the  service is re-
 stricted to kitchen waste.

 With the sole exception  of  Offutt AFB,  all communities permit residences to
 burn combustible wastes on their  premises,  either thru the  lack of no-burning
 regulations or the  ineffective enforcement of existing regulations.

                                   II-6

-------
In those communities where municipal collection service is not provided by
the governing body, the residents may employ private collectors or may haul
their own waste to the municipal dump which is frequently provided by the
.smaller communities.

Where on-site disposal is practiced,  and this must include all communities
"to some extent with the exception of Offutt,  the usual practice is to burn
combustible waste in  some informal and inefficient incinerator such as a 55
gallon drum locally referred to  as a burning barrel.  Many municipal officials
and  residents condone the practice  of burning clean dry combustibles in burn-
ing barrels.  Observation will reveal that burning barrels are used to burn
not only paper and other  clean dry combustibles but garbage  and other odor
and  smoke producing wastes.  This not only produces air pollution, smoke
and  odor nuisances,  residue for  rats,  and unsightly conditions; but also re-
presents a major source of fires requiring  fire department assistance.

Residential waste collection is a responsibility of the community and this
service  should be provided either thru the use of municipal forces and equip-
ment or thru a municipal contract.   On-site burning  of this waste would be un-
necessary if proper organized collection service is provided to all residences
in the community.    In Part IV  of this report, recommended ordinances  are
presented which provide  for collection of residential solid waste and forbid
the burning of waste in other than licensed incinerators.

Residential solid waste delivered to the major disposal  facilities was
measured during the landfill surveys described in Section E.  Also measured
was  the  residue from waste material burned on-site.  The  portion which was
not measured was that part burned  on-site.

A study  was conducted to determine the effect of backyard incineration on
domestic wastes based on quantities collected from routes  where incineration
of combustibles is extensively practiced as compared to routes where there
is little  or no incineration practiced.

While the quantity of ordinary domestic waste which will be produced by a
specific community depends upon the geographic location,  season of the year,
economic and social level,  and other special  community characteristics; the
major reasons for variation in domestic waste production are community
regulations and their enforcement,  and refuse disposal  services provided.

Because of variation from community to community,  exact data determined
by measurements are desirable  in order to provide a sound basis for deter-
mining a comparison.

Under similar  conditions the  amount of ordinary domestic waste produced
in a  community will be in proportion to the  population.   Refuse quantities are
usually expressed in pounds per capita per year and/or per calendar day.


                                   11-7

-------
 Two residential communities with small and medium sized lots and with  single
 and multiple family dwelling units were selected to determine this comparison.
 The two communities were Capehart Housing and Council Bluffs.  Capehart
 Housing, located at Offutt Air Force Base, has a population of approximately
 6600 people,  consists of 1803 family dwelling units,  offers complete collec-
 tion service,  and permits no on-site incineration.  Council Bluffs,  on the other
 hand,  offers partial collection  service  and allows on-site incineration.  A por-
 tion of Council Bluffs consisting of residential areas only, was  selected to ex-
 clude;  any influence of commercial waste.  It was anticipated that the additional
 per capita production of domestic waste collected from Capehart Housing
 would  represent the amount of  per capita domestic waste disposed of on-site
 by incineration in Council Bluffs.  However,  the opposite results were obtained
 from this survey. Council Bluffs produced approximately one-half pound more
 per capita daily domestic waste than did Capehart Housing.

 When  the selection of these  two communities was being considered it was
 recognized that Capehart was  a special community populated exclusively
 by military families,  but there was  an  excellent cross section of  senior and
 junior officers and enlisted  men,  living in dwellings varying from four-bedroom
 single family units to two-bedroom  multiple family units.  There were no
 transients and no barracks included in  this study.   Factors which may have
 influenced the results from  Capehart are that all dwelling units are equipped
 with garbage  grinders  and the community is relatively new, which would reduce the
 amount of tree wastes.   Whatever  the reasons may have been, the results were
 unuseable.

 The Study Area was extensively examined in  an attempt to find  suitable areas
 which  could be used in lieu of Capehart.  None could be found which were large
 enough for comparative purposes, and  which were not special for one reason
 or another.  As a suggestion to future  investigators in this field,  it will probably
 be necessary to measure a community's solid waste products under conditions
 which  allow burning and then remeasure the community after all burning has
 been effectively stopped.

 It was concluded  an estimate of the  quantity  of waste being burned would  be
 satisfactory,  since residential or domestic waste  represents only a small
 portion of a community's total  solid waste.  It was assumed that approximately
 50% of the dwelling units in  the Study Area have  some burning capabilities  and
 that 50% of the domestic waste is  readily combustible.  It was also assumed
 that the  burning facilities had  a 25% use factor.  A factor of 6% (. 5 x . 5 x .25 =
 .0625) was  calculated and added to the  quantity of domestic solid waste measured
 during the landfill surveys to compensate  for on-site burning of this waste.

JD.	SPECIAL STUDIES

         1.       General .  During the organization of this study,  it was recog-
 nized that there were several special waste  problems which could influence
 present  and future planning.  These special  wastes, though common to communi-
 ties, can present unusual collection and disposal problems.  Individual studies
 were conducted and analyzed to determine the influence they would have  on the
                                    II-8

-------
 aolicl waste program for the area.  These special wastes discussed in the
 following paragraphs include automotive vehicles and the related salvage
 industries, special tree waste  caused by Dutch Elm disease, meat packing
 industry wastes,  and commercial feedlot industry wastes.

         2.     Automobiles and Scrap Metal

                _a.    General  .  Abandoned automobiles,  auto  salvaging and
 scrap metal operations  were studied  to determine the extent of the solid waste
 involved.  It was  found that they do not present a solid waste problem of any
 significant magnitude,  although,  they do present many other serious  community
 problems.  It was also found that the auto salvaging and scrap  metal  industries
 are not understood by the general public.  In the following  paragraphs, data is
 presented to explain the function of these industries, the problems they create,
 what  can be done  about the problems  and why they do not create solid waste in
 any large quantity.

                Jb.    The Auto Salvage Industry .  The motor vehicle is a
 vital  part of our society affecting the general economic structure and life of
 the community.  The motor vehicle has  a definite life cycle. Based  on national
 averages, the motor vehicle  survival rate  is as follows;

          Years after Original            Percent of Vehicles
          	Registration	            	Surviving	
                   6                             95
                   8                             81
                  10                             56
                  12                             33
                  14                             18

 During its life  cycle the motor  vehicle will pass from a transportation unit
 to a valuable source of materials providing spare parts for other units still
 operable.  Eventually it becomes a natural resource of scrap metals to be used
 by the metal making industries.

 Information from  automobile.manufacturers and the salvage industry reveals
 the average total weight for an  automobile is about 3, 300 pounds,  of which 600
 pounds,  or 18% is not salvable metal,  such as  upholstery,  rubber mats, tires,
 hoses, insulation,  undercoating,  glass and plastics.    The balance of the weight
 is composed of various kinds of ferrous metals and non-ferrous metals,  such
 as copper, zinc, aluminum, lead, brass, bronze and  others.

 The auto salvage industry has been historically identified as the "junk yard, "
 which it is not.  It deals in the  salvaging of reusable parts for  the automotive
 industry.  With the tremendous and continuing increase of  automobile produc-
tion over the years, the auto salvage  industry provides a needed service to the
 community.  The  1985 predicted  motor vehicle  population of the United States
is estimated at 115 million.  A damaged automobile, economically unrepairable,

                                   II-9

-------
can provide many valuable and serviceable spare parts,  including partial body
sections,  for the repair of other less damaged vehicles.   Unsalvable or
obsolete parts are sold to the scrap metal industry.

This industry has a well deserved, bad reputation for aesthetic  conditions.
Recent Federal  Legislation in the form of the Highway Beautification Acts,
provides certain regulations concerning "Auto Wreckers" near or adjacent
to Federally Funded Highways,  and has brought  much attention to the industry.
These  regulations require certain fencing and screening  of the operations
under prescribed conditions.  They do not apply to many auto salvage opera-
tions in urban areas which must be controlled by other zoning laws or ordinances.
The auto salvager usually operates in an  industrial zone, but may operate in
other zonings through the legality of zoning variances.

The salvager normally  maintains a large and unsightly stockpile of auto hulks,
aJl potential items of solid waste.  When  the auto has been stripped of all
possible spare  parts, it is ready for the  conversion to scrap metal.  Most
scrap metal processors of auto hulks insist they be burned to rid them of  all
non-metallic material before they will be accepted as scrap  metal.  This  re-
quirement is more of an accepted practice than  an absolute necessity.  It
makes the metal processor's job easier and reduces his  costs but the open
burning of auto hulks is a nuisance to the community, a source of air pollution
and a fire hazard. Passage and strict enforcement of anti-burning laws are
necessary to curb this  practice. Auto hulks can be processed for metal
salvage without  burning and are  processed this way in many  communities.
Elimination of burning  will create some additional costs to the industry;
however,  this is a problem for  the industry to overcome as  a part of doing
business.

The problem of large inventories of auto  hulks is a problem  the  salvage industry
has, and will continue to have as long as  scrap rnetal prices remain at the
present low level.  New metal making methods have lessened the demand  for
scrap metal and consequently the price has been substantially reduced.  Many
salvagers stockpile auto hulks hoping for future   price increases, and move
out hulks  only to make  room for newer models.

The survey included 55 salvage yards in  the Study Area and  revealed an esti-
mated  39, 500 hulks on  hand.

The problem confronting all scrap processors in the Study Area has both
technological and economic roots.  It begins with the fact that steel mills  have
reduced their reliance  on scrap as  a raw material.  This is  due to the  installa-
tion of new types of steel making furnaces and the reluctance of  some large
integrated mills to accept automobile scrap in large tonnages.

Whenever demand for scrap drops,  auto  scrap is most affected.  It is probably
the most difficult and expensive  type of scrap to prepare.  Besides the ton of
usable ferrous  scrap, a car contains copper,  lead, plastics, glass and other

                                   11-10

-------
 non-metallic materials.   All of these can be poison to a batch of steel.  They
 should be removed by the processor to produce acceptable steel scrap.

 To meet this demand, many scrap processors have installed large and expen-
 sive shredding devices such as the one in Council Bluffs, Iowa,  which tear and
 shred an anto hulk into small pieces, including the steel hulk, the glass,
 rubber,  dirt, and plastic.  The steel is removed from the non-magnetic mate-
 rial by magnetic separation.   The remaining material is sometimes picked over
 for  copper or other metals but it is mostly waste  to be disposed of at a landfill.
 The magnetically separated steel is high grade scrap, relatively free  of the
 chief contaminant, copper.  This high grade scrap is worth from $13 to $36 a
 gross ton delivered, depending on the area. From this price the processor
 must deduct transportation costs, production costs,  the  cost of daily operation,
 and  his return on his investment.  Only then can he figure what he can pay for
 his  raw material, the old car  itself.  Ten dollars to $12  for a car can often be
 considered to be a fairly good price.

 Operators estimated that  approximately 40% of all vehicles on hand would be
 disposed of with an  appreciable increase in the price  of scrap metal.  The
 yards  surveyed occupied approximately 212 total acres, with an average of
 about 188 vehicles per acre.

 In general,  the housekeeping practices of the  auto salvage industry are poor,
 contributing  to the public demands that something be done to  clean up this
 industry.  Part of the problems are inherent in the nature of the work. Sal-
 vage yards are difficult to maintain in an acceptable  and  nuisance-free condi-
 tion, but it can be done.  A few of the  operators have made attempts to screen
 their yards and present a decent appearance.   They would do more if the  in-
 dustry was required to conform to currently existing  ordinances and zoning
 regulations.

 Although many hulks are retained in hopes of improved scrap prices, many
 accumulate simply because it  costs more to load and haul the hulks to the
 metal  salvager than they are worth.   The stripped hulk at this stage is an
 industrial waste  to the  auto salvager.  By allowing the hulks to accumulate,
 the operator is postponing the expense of disposal.  If he were required to
 site  screen his yard and control the weeds and insect breeding conditions
 around these old hulks, more of them would be promptly removed to the
 scrap metal dealer.

 The  auto salvage industry in the Study Area has a potential solid waste  problem
 in the large inventory of auto hulks.   This  potential will not become  a problem
 of disposal to the community while there is a market for the  scrap metal. Even
 though it may cost the salvager more to haul a hulk to the scrap dealer than
 he is paid for the hulk, it  is more economical than hauling the hulk to a muni-
 cipal disposal site and receiving nothing or being charged to dispose of it.

Strict enforcement of ordinances in the Study Area pertaining to operating
 conditions in and around salvage establishments is necessary to improve

                                   11-11

-------
aesthetic conditions and reduce the health and fire hazards for the community.
Enforcement of these regulations may cause a temporary surge of auto hulks
onto the local scrap market, but we believe this would be a minimal problem.
Somo minor costs to the salvager will resultj  but this must be considered as
a cost of doing business.

The  auto salvage industry plays an important role  in the community.  However,
they must be required to conduct their business in a manner that it will not
interfere with the welfare of others.

               _c.    Scrap Metal Industry.  The  scrap metal industry is
responsible for the final phase in the life cycle of the automobile and the
source of other salvaged metals before they are reclaimed in new metal making
processes.  This industry has provided  over 40 million tons per year of scrap
metal for metal making industries and foreign exports.  Over 40% of the nation's
copper and more than  1/2 million tons of lead is recovered annually by the
scrap metal industry.   The automobile hulk accounts for about 5 million tons of metal
per year.

This industry experiences many of the same problems outlined for the  auto
salvagers.  Large  stockpiles of processed scrap are often on hand due  to the
lack of demand for the product.  Large and expensive machinery is required
to process the metals and auto hulks and the operation is  seldom confined
within buildings.

The  price being paid for processed scrap today is  not high enough in  many areas
to allow the processor to go out extensively for automotive hulks as a source of
materials.  It is not high enough to encourage many graveyard operators and
others to ship cars to processors at their own  expense.

There is absolutely no question that the  scrap industry could process every car
in the Study Area available  for  scrap with its existing production capacity.  The
scrap processor in Council Bluffs can process 400 to 500 auto hulks in a  single
normal working day, and is a good example of  the  capability of present techno-
logy.

                dL    Abandoned Automobiles.  The present problem of aban-
doned automobiles in the Study  Area does not appear to be large.  Most old and
unserviceable vehicles  find their way to the scrap metal dealers.

Unserviceable  or abandoned automobiles on private property are considered
the problem of the  property owner.  If abandoned on a public street or  property,
the City will haul it away,  impound it, and attempt to locate the last  registered
owner.  If located, the  last registered owner is usually responsible for any  cost
incurred during impoundment.  Periodically the impounded vehicles  are auc-
tioned to the highest bidder.  Impound costs are deducted from the bid  price and
the balance,  if any, is sent to the last registered owner,  if he has responded to
the: previous notice.  Where no owner can be found, auction proceeds are  retained
by the City.
                                  11-12

-------
 The present handling of abandoned vehicles in the Study Area is generally
 adequate considering the number of vehicles involved.  Abandonment may
 increase if salvagers become reluctant to receive vehicles too old for parts
 ov salvage value, if new operating regulations are enforced.  No serious
 problem is anticipated.  Improved vehicle identification methods,  strong
 enforcement,  and proper penalties for abandonment of vehicles,  should
 control  any increase.

                jj.    Automobile Disposal by Municipalities.  With the in-
 creasing cost  of processing of auto hulks, and the passage of air pollution
 regulations, it is possible  that salvagers will be reluctant to receive or pay
 for hulks for scrap purposes.

 If this were to happen, it is possible to dispose of auto hulks in landfills.
 During a previous  solid waste study an experiment was conducted at a muni-
 cipal disposal  site to determine what volume would be required for an average
 hulk.  A 1957,  medium priced station wagon,  including upholstery, frame and
 heavy undermetal, but excluding the engine block, bumpers, wheels and tires;
 a typical abandoned auto type, was placed right side up on level ground.  A
 landfill bulldozer was used to crush the hulk.  The operation took approxi-
 mately five minutes,  reducing it in volume from about 432 cubic  feet to less
 than 108 cubic  feet, or 4 cubic yards.
 The compacted hulk was easily included with other waste  and covered with
 earth.  This is a poor ending for a proven natural resource, but  indicates
 disposal by landfilling is practical.

 Many landfill operators do not wish to be bothered with crushing  and burying
 auto hulks.  They are a bother but it can  be done economically and is a
 satisfactory way to dispose of hulks that become a burden to the community.

                f_.    Laws and Regulations.   The auto salvage and scrap
 metal operation, and the abandoned vehicle are technically not a  solid waste
 problem.  They are; however,  a community problem requiring proper con-
 trol insofar as they affect the  health, safety and well being of the community.
 Existing ordinances and regulations are not adequate for  several reasons.
 In some  instances,  they are unrealistic and consider auto salvaging, the
 scrap metal industry, junk yards and pawn brokers as being the same.  Each
 are different and should be treated separately.  Some requirements are not
 practical and if enforced would require unwarranted expense not  only to the
 industry but to the  municipalities.  In other cases,  there  are inadequate re-
 quirements to  protect the public.  As a result,  there is little effective en-
 forcement of existing laws  and regulations.

 Laws of  the various communities should be reviewed and amended to be
 realistic and effective.  Of particular importance are zoning regulations;
 provisions to outlaw all open burning; requirement for fencing and  that opera-
 tions be  conducted within fenced areas and not in the  public right-of-way; and
 rodent, weed and insect control.   All communities should consider an ordi-
nance which would  class  all inoperative motor vehicles  on private property
in residential zones, and not properly garaged, as "litter" and require removal
 or proper  storage.
                                   11-13

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The City of Council Bluffs is a prime example of what can be accomplished
by proper enforcement of this ordinance.  The offender is served a removal
notice and allowed  a reasonable amount of time,  generally from 5 to 30 days,
to clean up the nuisance.   If the offender does not comply with the notice
within the allotted time, the offender must appear in court and is generally
fined.  Approximately 2000 non-licensed or junked cars  located in backyards,
in and around the city,  have been removed since  February 1966 by enforcing
this litter ordinance.

                   Auto Salvaging Industry Statistics

Sampling Group;

Auto salvage operations observed and interviewed within Study Area:  55
Estimated total wrecked vehicle inventory on hand:  39, 500
Estimated total acres  occupied by Salvagers, Study Area:  212
Estimated wrecked vehicles per acre, on hand:   188
Estimated hulks immediately available from current inventories, with
improved market conditions:  15,800 (40.0%)

Study Area;

Estimated current  monthly scrapping rate:  1,075 vehicles.
Estimated 1968 vehicle registration:  214,300
Estimated yearly scrapping rate, Study Area: 6% of registration
Estimated yearly scrapping rate, Nation: 7% of  registration
Estimated average net increase in yearly registration, Study Area;  4%
Estimated average net increase in yearly registration, Nation:  3%
Estimated rate  of vehicle  registration and scrapping,  Study  Area;
                   Registration          Scrapping @ 6%
            1968      214,300                12,900
            1969      222,700                13,400
            1970      231,100                13,900
            1975      273,100                16,400
            1980      315,100                18,900
            1985      357,100               21,400
            1990      399,100               23,900
            1995      441, 100               26,500
Estimated Total Scrapped Vehicles,
                           1968-1995      550,700

         3.     Special Tree Waste .

                a_.     General.  In a large community or metropolitan area
the influence of any single industrial or commercial firm or groups of allied
firms usually has little influence  on  the total solid wastes of the community.
They  could double their waste  or  eliminate it completely,  and still have little

                                   11-14

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immediate effect on the magnitude of the community's solid waste facilities.
Over a long period of time their influence might eventually be felt but there
would be ample time to anticipate the  changes necessary.

Changes in population trends  and in per capita waste contributions are suffi-
ciently gradual that they too can be anticipated by solid waste managers in
time  to make  any necessary changes.

Problems that can  become serious in  the management of solid waste disposal
must involve at least two elements; (1) large quantity changes either increases
or decreases;  and (2) a short time during which the change takes place.  Wastes
resulting from the  removal of large quantities of diseased American Elm
trees in a short period of time meets these two items of criteria and could
be a problem  if not anticipated.

American Elm trees are being killed by the Dutch Elm Tree Disease in great
number in recent years.  The disease is caused by a fungus named
Ceratocystis Ulmi  which is carried by the European Elm Bark Beetle.  Fungus
spores are spread  from diseased trees to healthy trees by the beetle and enters
the healthy trees through openings in the bark of twigs caused by feeding in-
sects.  The disease was first  found on the east coast about 1930 and since that
time has spread throughout the east, north to Canada and into the south.   At
the present time it has worked as  far west as Iowa,  Nebraska,  Kansas and
Missouri.

Dutch Elm disease  was first found in the Study Area in I960.  By 1963 there
were 22 known cases of infected trees and 80 suspected cases.

It is estimated that, since the discovery of the  Dutch Elm disease in the Study
Area, 35% of  the 613, 355 original elm trees have been removed or are presently
diseased and must  be removed.  By the end of 1968 approximately 214,674 diseased
trees had been removed,  most of which have been disposed of by open burning
at public sites. Few volume or weight records have been maintained; therefore,
future volumes and weights are based on known properties of elm wood, existing
estimates, and information developed in cooperation with city,  state and federal
foresters,  and county  agents.

At the present rate of  loss, it is estimated that most  of the American Elm trees
in the Study Area will  be diseased by 1973.  The  greatest quantity of these
trees for which solid waste disposal facilities must be provided are located
in the cities of Omaha, Bellevue, Council Bluffs  and the immediate  area.  This
amount of  special tree waste is estimated to be  306,984 elm trees,  or 595,550
tons.  The amount  of special tree waste in remote or rural areas which pro-
bably will not  be removed or will not be brought to solid waste disposal facili-
ties is estimated to be 91,697 elm trees  or  177,892 tons. This  latter amount
of special tree waste is not included in the  quantity for which disposal must be
provided. See Appendix Exhibit II-1 for Elm Tree Statistical Information.

During the landfill  surveys discussed  in Section E of this Part II the  quantities
of waste from diseased elm trees were recorded separate from the  other

                                  11-15

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wastes.  To the above quantities which were measured, additional estimated
quantities were added to reflect those quantities which were disposed of
on- site.  The sum of the measured quantities and on- site quantities  repre-
sent the total  diseased elm tree wastes.   These are shown  as Special Tree
Wastes in Table 11-24.

Since the Special Tree Wastes represent approximately 17% ot the total
waste, it is an important segment of the total. Only approximately  1/6 of
this material  was measured at public disposal facilities.  The remaining
5/6 were disposed of elsewhere.  If proposed regulations and controls con-
cerning landfills and air pollution are adopted and enforced these 5/6 will
appear at public disposal facilities  and must be anticipated. There must be
adequate landfill capacity and  equipment to handle these significant quanti-
ties.   Once the  capacity to  handle the predicted quantities is available,  the
reduction in quantity expected in 1973 must also be anticipated,  because the
schedule of fees to finance the operation is based on expected quantities.
The fee structure and its relationship to expected quantities and fixed and
variable costs are discussed in Part III.

        _b.      Disposal .  Elms killed by Dutch Elm disease can be used
for fireplace wood, provided the wood is burned before spring.   If only a
portion of the  cut wood is used, beetles emerging in the spring  from the
remaining  logs  will carry the  fungus to healthy elms.   To prevent this from
occurring, the wood should be stripped of bark or thoroughly sprayed with
a suitable chemical which will kill the beetles.  The fungus is not spread
by the ashes or srnoke from infected elrns.

Investigation indicates that elm wood  has few commercial or industrial uses
arid then only  ii' the user is close to the  source of material  to rediice shipping
costs. Elm wood is used for making  pallets, dunnage,  furniture and veneer,
although the demand is very small.  The physical properties of elm  wood pre-
clude its use as structural  material.  It tends to  split and twist when drying.
The largest consumers of elm wood are the pulp mills making fiberboard,
corrugated boxing  and particle board  and similar material. There are no
pulp  mills located in the immediate area currently processing elm  wood and
the more distant mills expressed little or no interest  because of excessive
shipping costs;  therefore,  this outlet was not considered further.

Many mills refuse  to accept city elm trees for chipping because of operating
problems  resulting from the presence of tramp iron.   Marketing elm wood
for pulp purposes is not recommended.

Elm wood as a fuel for power  plants was considered.  It woul d again have to
bo chipped. Alter chipping, the elm fuel would cost more  per useful Btu
than coal.  This outlet was not considered further.
      killt-d by Dutch Elrri disease can be disposed of by incineration or open
burning.  It is estimated that incineration of mixed solid waste costs
 several tunes as   much as disposal by sanitary landfill methods under present
                                  II- 16

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 conditions in the Study Area.  In the preceding paragraph it was stated that
 the chipped elm wood cost more  per useful Btu than coal.  It is apparent that
 incinerators which would burn the elm wood are not feasible even when con-
 sidfering waste  heat recovery.  No further consideration was given to incinera-
 tion of elm tree wastes.
   t
 It is possible to burn  the elm trees in open fires.  Although logs are difficult
 to burn, a proper  arrangement could be made which would reduce most of
 the wood to ash.  It would be possible to control such a burning operation
 from becoming a fire hazard although a considerable amount of land prepara-
 tion and labor would be required. This method is not recommended because
 of the  air pollution problem that  would be created and the expense involved.

 Diseased elm tree waste can be properly disposed of in sanitary landfill  sites,
 separately or with other solid waste of the community.  When filled separately,
 many  sites would be available that might not be available for mixed operations.
 This is the only advantage.  When filled alone, considerably more  earth  is
 required.  Logs are particularly difficult when handled alone.   They pile up
 one upon another and  make a very difficult surface upon which to work land-
 fill equipment.  The limbs are not adequate to solve this problem.   Large
 quantities of earth are required to fill around logs to make a stable mass.

 When filled with other solid waste from the community, the other material
 packs  around the" logs making  a satisfactory  working surface.  Only cover
 dirt is  required.  With the other  material adding  to the  total volume, the
 unit operating cost of the operation is  reduced. It is less expensive to bury
 the elrn tree waste with other  solid waste than to  bury it in a site separately.

 The cost of operating  a sanitary landfill in the Study Area has been estimated
 to be $1.40 per ton.   This is the  most economically  acceptable way to dispose
 of the  diseased  elm tree wastes.

        4.      Meatpacking Industry  Waste.  Included  in this  category are
 solid wastes from  slaughter plants and their holding pens,  and the  pens of
 the central  stock yards.  None of this  material was measured at any of the
 landfill surveys described in Section E; therefore none is included in that
 quantity of waste which was disposed of at public  disposal facilities.  Currently
 these materials are being disposed of  through  public sewers,  piled on the pre-
mises  of packing plants,  hauled to farm land or dumped at a  railroad siding.
 These  materials were studied  and are included in the Commercial  and Indus-
trial Surveys described in preceding Section B.   The solid waste from the
 Omaha slaughter houses will continue  to be  flushed to public  sewers for
treatment.  These  quantities were given no further consideration in this re-
port.

It has been assumed that packing plants will not be permitted to continuously
pile solid  waste on their premises; that haul to farm land disposal will be
uneconomical; and  that dumping  of pen waste without adequate sanitary  land-
fill facilities will not be permitted.  Experience in other cities has shown that

                                  11-17

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iii recent years packing industries have been required to dispose of this mate-
rial in a sanitary manner in order to eliminate the odors caused by the de-
composition of the organics and the problem of rat and insect control.

Paunch manure can be treated or disposed of using a variety of methods.
It can be incinerated, dried or otherwise processed  for feed,  or placed in
sanitary landfills.  Incineration is considerably more expensive than sani-
tary landfilling and is not considered further in this  study.  Feeding of paunch
manure has been tried and abandoned  over a period  of years.   Currently
there are new attempts being made to feed paunch manure.  For purposes
of this report it is assumed that paunch manure is a waste product for which
disposal is necessary.

The industry has found that the most economical acceptable way to dispose
of paunch manure and pen sweepings in an area like  this Study Area, is to
use a sanitary landfill.  Capacity to accommodate the expected quantities
of meat packing industry solid waste has been included in the  estimates for
public  sanitary landfills to be provided for present and future needs of the
Study Area.

In addition to  the existing meat packing industry, which changes from time
to time in quantity of kill and waste produced, a new major facility is being
constructed in Council Bluffs. This new industry will be completed in 1970
and is  expected to kill approximately 2000 cattle per day or 572,000 head
per year.  This industry and public officials of Council Bluffs are planning
to dispose of the  paunch manure, peck manure,  and pen sweepings in public
sanitary landfill facilities.  Estimates of  these wastes are also included in
estimates of required  public sanitary landfill facilities.

The annual quantities of paunch manure, peck manure , and pen sweepings
expected from the meat  packing industry in the Study Area for disposal in a
sanitary landfill are estimated to be 16,900 tons or  19,469  cubic yards
(compacted).  Since these quantities are estimated for the  current year,
no seasonal adjustment is necessary.

These  quantities  are  based upon'calculations shown in Table H-4 and were
used as part of the  total present quantities of commercial and industrial
wastes  summarized in Section H.
                                   11-18

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TABLE II-4.  MEAT  PACKING INDUSTRY WASTE QUANTITIES
    Beef Kill;
    a.  Council Bluffs (J970)
        2000 head per day,  5.5 days,  52 weeks
    b.  Omaha Packing Industry
        4895 head per day,  5.5 days,  52 weeks

    Paunch Manure Waste:
    a.  Council Bluffs (1970)
        Weight @ 48 pounds per head
        Volume @ .77 cf per head
    b.  Omaha Packing Industry
        Weight @ 48 pounds per head
        Volume @ .77 cf per head

    Pen Sweeping Waste:
    a.  Council Bluffs (1970)
        Weight @ 10% of paunch manure
        Volume @ 20% of paunch manure
    b.  Omaha Packing Industry
        Weight @ 10% of paunch manure
        Volume @ 20% of paunch manure
    Disposal of Packinghouse Waste;
    a.  Council Bluffs (1970)
        Paunch and peck manure, pen sweepings
    b.  Omaha Packing Industry
        Paunch and peck manure
        Pen  sweepings

    Packinghouse Waste  to Sanitary Landfill:
            Annual Quantity

            573,000 head

         1,400, 000 head
             13, 728 Tons
             16,296 CY

             33, 600 Tons
             39,886 CY
              1,372  Tons
              2, 745  CY

              3, 360  Tons
              7,977  CY

              Method
       Council Bluffs (Future)
        Paunch and peck manure
        Pen sweepings
       Omaha Packing Industry
        Pen sweepings
                          Total
Tons/year
  13,728
   1, 372

   3,360
 18,460
           Sanitary Landfill

           Internal Process
           Sanitary Landfill
CY/year
 16,296
 2, 745

 7.977
27,018
    Compaction Factor Adjustment:
    The following compaction factors were assigned to each material
    which adjusts the "as received"  volumes to the volumes which the
    materials would occupy when mixed with other materials  and  com-
    pacted into a sanitary landfill.
                             11-19

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    TABLE II- 4.  MEAT PACKING INDUSTRY WASTE QUANTITIES (Cont'd)

7 •      J~ype_of Waste:
             _
         Paunch and peck manure (Council Bluffs) @  .8 x 16,296 = 13,036
         Pen sweepings (Council Bluffs)           (5)  . 6 x  2,745 =  1,647
         Pen sweepings (Omaha)                  @.6 x  7,977 =  4, 786
                                   Total                         19,469 CY/year

8.       A total volume of 19,469 cubic yards per year (compacted in  place)
         represents the expected meat packing industry waste from the
        Omaha-Council Bluffs Metropolitan Study Area.   This material
         increase  has been projected at the same annual rate as other
         commercial and  industrial wastes


         5 .      Disposal  of Fecdj.pt Wastes.

               _a.   General .  The livestock feeding business has emerged
from small individual farm operations to large-scale enterprises in which many
thousands of animals are  fed in confinement.  Until the early  1950's,  small-
volume farmer-feeders accounted for nearly all the Study Area's livestock
production.  These feeders still produce more than half the livestock,  but
commercial lots have grown rapidly.  Nationally, the number of livestock
fed in large commercial lots has increased about 40% in the last four  years
which is approximately six times as fast as the number fed by farmer-feeders.

The shift in agriculture, and animal feeding in particular,  from family- sized
operations to large commercial enterprises is following the same pattern
as other industry; larger  operations are necessary to take advantage of
mechanization, which requires  specialization, management,  and huge  sums
of capital.

               -^'   Survey.   A survey was conducted to determine the dis-
posal methods of  animal  solid wastes from the various commercial feedlots
in the Study Area.  For purposes of this study, commercial feeding of cattle,
swine,  sheep and  poultry is defined as those  operations which feed 1, 000
animals or birds at one time.  The  survey was limited to commercial feeders.

The purposes of the survey were to determine the current disposal methods
being employed; whether the individual feed lot operators had plans for signi-
ficant changes in disposal methods in  the foreseeable future; and whether
changes in methods might be necessary in the public  interest.

There were 49  commercial feed lots in the Study Area feeding 1,000 or more
head of cattle at one time.  The size and number per county were as follows:
                                   11-20

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                                          Number of Feed Lots
         Douglas County:
                1000 to 2499                         6
                2500 or more                       10
         Sarpy County:
                1000 to 2499                         9
                2500 or more                       10
         Pottawattamie County:
                1000 to 2499                        12
                2500 or more                        2

         Total Three Counties:
                1000 to 2499                        27
                2500 or more                       22
                                                    49

There were no commercial feed lots in the Study Area feeding 1000 or
more head of swine at one time.

Data was obtained concerning sheep and poultry feeding operations.  The
quantity of solid waste is insignificant to the total area quantities but is
included in the quantity summaries which follow.

                _c.    Quantities.  The daily production of manure from farm
animals,  as determined by a number  of investigators in  animal waste manage-
ment,  is approximately as shown in Table II-5.

TABLE II-5.  AVERAGE DAILY MANURE PRODUCTION AND COMPOSITION

Item	Unit	Swine   Poultry   Sheep   Turkeys   Cattle
Wet Manure
Total Solids
Volatile solids
Nitrogen
P20s
K20
Lb/d
%
%
% db
% db
% db
7.0
16.0
85
4.5
2. 7
4.3
0.25
29.0
76
5.6
4.3
2.0
3.0
34.0
66.0
1. 1
.3
.9
0. 75
26.0
78
5.2
2.8
1.9
64.0
16.0
80
3.7
1. 1
3.0
The estimated annual production of manure from feedlot animals in the Study
Area is given in Table II-6.   The annual production of feedlot  manure was
determined by multiplying the numbers and types of feedlot animals obtained
in the feedlot survey by the average daily manure production given in Table
II-5.
                                   11-21

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     TABLE II-6.  ESTIMATED ANNUAL MANURE PRODUCTION -
                   COMMERCIAL, FEED LOTS IN STUDY AREA

            No.  of Animals Fed per Yr.   Animal Waste -  Tons per Yr.
Livestock   Seasonal Continual   Total    Seasonal  Continual       Total
Cattle
Swine
Sheep
Poultry
12,400
0
4,000
30,000
243,000 255,700
0 0
11,000 15,000
37,000 67,000
59,520
0
900
562
1,420,872
0
3,012
1,688
1,480, 392
0
3,912
2,250
Seasonal - refers to 1 - crop of animals fed for a period of 5 months or 150 days.
Continual- refers to2 - crops of animals fed for a period of 1 year or 365 days.

                cl.    Fertilizer Value .  Until the development of the fertilizer
industry,  green plants and animal manure were the main source of  supplemental
plant nutrients.  Today, in light of the plentiful supply of commercial fertilizers,
the question has been  raised if it pays to collect and use animal manure as
fertilizers.  An analysis of the manure and a look at the feedlot disposal
methods indicate that  the application of manure on soils is well justified and
desired.  It is justified because animal manure contains plant nutrients which
have agricultural  and  commercial value even though, in some parts  of the
country the commercial value of manure cannot compete with mineral ferti-
lizers.

If sufficient land is available, field  spreading  of the manure should  be encour-
aged because it provides an adequate treatment and final disposal of the wastes
at the same time.

                _e.    Method of Animal Waste Disposal.  By far the  predomi-
nant method of handling feedlot manure in the  Study Area is by accumulation
of a manure pack, followed by field spreading.  In most of  the Study Area,
the manure cannot be  placed on the  fields daily because of climatic  factors,
cropping practices, labor, or other reasons.  Some storage is usually required,
and, in many instances, this is accomplished  by permitting manure to accumu-
late in the buildings or on feedlots.

If manure is not removed from the buildings or feedlots,  bedding or litter must
be used to absorb and  conserve the  liquid portion of the manure and to prevent
the animals from  getting dirty.  Use of bedding or litter requires that it be
handled and stored, and, in many areas, bedding material is both scarce  and
expensive.  Consequently, there is  a trend toward producing livestock without
the use of bedding.

In the Study Area, manure is handled primarily with mechanical equipment.
The removal and spreading of feedlot wastes is normally accomplished using
tractors nnd manure spreaders. Equipment normally used in other farming
operations is adaptable to handle feed lot waste.

                                   11-22

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 Stockpiling of animal feedlot wastes followed by field spreading will continue
 to be the predominant method of handling and disposal for the average feedlot
 operator in the Study Area.  All feedlot operators plan to dispose of the
•animal wastes by spreading the material on their own crop  land, or on
 adjacent farm land,  and to use the animal wastes as a soil conditioner or
 supplemental fertilizer.  None of  the feedlot operators propose changes in
'their method of animal  waste disposal or expressed intent to dispose of this
 material in a sanitary landfill.

 The present method  of animal feedlot waste disposal is considered adequate
 for the Study Area providing that the manure stockpiles are not allowed to
 remain on the premises indefinitely and that field spreading is followed by
 discing, or plowing, in  such a  manner  that the animal waste is thoroughly
 incorporated into the soil and disposed of in a nuisance free manner.

 When determining the capacity of  public sanitary landfills which are recom-
 mended in Parts III and IV no provision has been made to include any signi-
 ficant quantities of solid waste from the animal feeding industry.

 The disposal of animal  solid waste on land in an acceptable method but if
 not handled properly can result in serious water  pollution problems.  Water
 pollution caused by runoff from feedlots can be as detrimental to a receiving
 body of water as that resulting from the wastes from other  industries and
 from cities.  Many of the feedlols  in the Study Area have grown with little
 planning and concern for the nuisance and pollutional characteristics of the
 feedlot;  and have  been established  in areas where the  capacity of streams to
 dilute  and assimilate feedlot runoff is severely limited.

 The water pollution problem associated with feedlot wastes is  basically a
 drainage problem.  As  a minimum, dikes should be erected around a feed-
 lot to protect the  receiving stream from feedlot runoff.  Also, rain falling
 outside the feedlot area should be  diverted around a feedlot and kept separated
 from feedlot drainage.  Feedlot runoff  has been found to produce a slug load
 effect  upon the receiving stream,  to be high in ammonia, and to contain high
 bacterial counts -- all of which are detrimental to fish and  animal life.

 Feedlot wastes  should not oe discharged into public waterways unless they
 are pretreated sufficiently to meet the  legal requirements established by the
 local and state public health  authorities.

 E.       LANDFILL, SURVEYS
         1.     General.   A seven-day surveillance was established at each
of seven major public disposal facilities in the Study Area.  These disposal
facilities were continuously manned by one or more technicians except when
officially closed and secured in a manner to preclude deliveries  of waste.
The Omaha Incinerator and Council Bluffs Landfill which have little traffic
were manned by their own employees who filled  out the field data forms.

                                    11-23

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The Omaha City Dump Site and the Council Bluffs Landfill were open for
5 days per week.  The remaining facilities were open 7 days per week.
The sites and the  dates of the survey are given in Table II-7.

      TABLE II-7.  DAYS AND DATES FOR LANDFILL SURVEYS
Locations & Dates
Sarpy Co. San. Landfill
9/10 to 9/15 fe 9/23/68
Omaha Incinerator
9/13 to 9/20/68
Council Bluffs Landfill
9/18 to 9/24/68
Douglas Co. San. L'fill
9/24 to 9/30/68
1st
T
F

W

T
2nd
W
S

T

W
3rd
T
S

F

T
4th
F
M

M

F
5th
S
T

T

S
6th
S
W



S
7th
M
T



M
Morse's San.  Landfill     W     T     F    S     S       M   T
10/2 to 10/8/68
Council Bluffs Dump      W     T     F    S     S       M   T
10/9 to 10/15/68

Omaha City Dump         M    T     W    T    F
10/21  to 10/25/68

The purpose of the site surveys was to determine the quantity and charac-
teristics of solid waste being delivered to places of disposal,  plus other
valuable data  which could be acquired  at the same time.  Most of the solid
waste  being generated in the community must be removed from the source
at regular intervals.  Thus if a continuous surveillance is maintained during
the course of  an entire week the information acquired will be representative
of the waste being generated.   The data acquired must be'adjusted and supple-
mented with other data.  This data is the major source of information con-
cerning the solid waste of the community.

Solid waste as received at a place of disposal is an extremely heterogeneous
material.  The usual way to determine the characteristics of the material is
to analyze representative samples as received.  A different approach was
taken during the landfill surveys.  Each load as it arrived at the disposal site
was viewed and the type of material in the load recorded.  Where there was
a mixture of materials, an estimate of the percentage of each material was
made.   Certain anticipated mixtures were considered as material classifica-
tions in themselves.  An explanation of the  development of the  unit weights
for the various material classifications is included in the Appendix as
Exhibit II-2.

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This approach would have been impractical without the use of computers
which are able to process the large quantity of information (more than 4400
loads were received and recorded).  By knowing the characteristics of the
•materials and the total quantity of each, it is possible to make reasonably
accurate estimates of  the solid waste of the entire Study Area.

While the quantity and types of materials were being recorded, other infor-
mation was also obtained.  The nature of this  information and how it was
processed and used is described in the following paragraphs  concerning
major computer programs, and in various other sections of the report.

The data was  recorded on the "Disposal Surveillance Questionnaire" which
is shown in Figure II-1.

The questionnaire form and the explanation of each item is as follows:

         ITEM NO. 1.   BOOK NUMBER   The book number was
         an internal processing control number and is of no
         importance to the data.

         ITEM NO. 2.  MONTH AND DAY   The month  of the year
        was recorded in  spaces 4 and 5.  For example,  September
         was recorded as 09 and October as 10.  Similarly, the day
         of the month was recorded in spaces  6 and 7.   For example,
         the 15th day of September was recorded as 15.  The year
         was not recorded on the forms.

         ITEM NO. 3.  TIME   The time  was recorded on a 24-hour
         basis in spaces 8,  9,  10 &  11; i.e.  0800 indicated 8:00 A.M.
         and 1310 indicated 1:10 P.M.  This was the time at  which
         the vehicle  arrived at the disposal facility.

         ITEM NO. 4.   LICENSE .CODE   The state in which the
         vehicle was licensed was recorded in space 12.  Code 1 was
         used  for Iowa, 2 for Nebraska, and 3 for  any other Staf<= or
         for Federal vehicles.
         The number designating the Iowa or Nebraska Counties in
         which the vehicle was licensed was recorded in spaces 13 and
         14.  If this was not appropriate or if  the vehicle was not
         licensed in Iowa  or Nebraska, Code 00 was used.

        ITEM NO. 5.   TYPE OF VEHICLE   The type  of vehicle was re-
         corded in spaces 15 and 16.  If the vehicle type was not  one
         of the nine listed, then a description  of the vehicle was written
         in the space provided  in Type 10  "Other".
         Note:  Vehicle type 4, or light trailer was one  that could be
               pulled  behind an automobile.   For  heavier trailers
               vehicle type 5 was used.

                                  n-25

-------An error occurred while trying to OCR this image.

-------
 ITEM NO.  6.  TYPE OF HAULER  The type of hauler
 delivering material to the disposal facility was recorded
 in spaces 17 and 18 if entirely of one hauler classification,
 and 21 and  22, and possibly 25 and 26,  if the hauler was
 a combination of hauler classifications.  If the hauler was
 entirely of  one classification no percent was recorded in
 blank marked %.  The computer automatically listed 100%.

 If the hauler was a contractor delivering general construc-
 tion wastes to the disposal facility, hauler classification 1
 in space 18 was used.  Similarly, if the contractor was de-
 livering wrecking or demolition wastes, hauler classifica-
 tion 2 in space 18 was used.  Any hauler regardless of his
 type,  hauling elm tree removal material to the disposal
 facility was coded using hauler classification 3 in space 18.

 If the hauler was a commercial hauler,  operating a route,
 hauler classification 4 or 5 or  6 or a combination of these
 numbers, or  all of these numbers was  used as appropriate.
 For example,  if the load was all domestic material, hauler
 classification 4 in space  18 was used.   Similarly, hauler
 classification 5 or 6 was used if the material was all com-
 mercial or  all industrial.  Whenever the commercial hauler
 delivered a combination of domestic, commercial,  and/or
 industrial wastes,  both the numbers indicating hauler
 classifications and the percentages of each was used,
 using the spaces marked %.  If the waste was entirely
 of one hauler classification, the computer printed out
 100%; therefore, no percentage was recorded in spaces
 marked %.

 If the hauler was delivering commercial waste of one source,
 hauler classification 7 or 8 was used  as appropriate in
 space 18.

If the haulers were public vehicles or contractor's vehicles
which were  hired by  a municipality for  collection and disposal
 of solid wastes, hauler'classification 9 or 10 or 11  or  a com-
bination of these numbers, or all of these numbers  was used
 as appropriate.  For example,  if the load was  all domestic
material, hauler classification 9 in space 18 was used.
Similarly,  if the material was all  commercial  or all in-
dustrial, hauler classification 10 or 11 in spaces 17 and
 18 was used.  Whenever the hauler delivered a combina-
tion of domestic, commercial,  and/or industrial wastes
both the numbers indicating hauler classifications and  the
percentages of each was recorded using the spaces  marked
%.  If the waste was entirely  of one hauler classification,
the  computer  printed out 100%; therefore, no percentage
recorded in spaces marked % was required.

                          11-27

-------
If the hauler was any other public vehicle,  hauler classification
12 in spaces  17 and 18 was used.

If the hauler was a private citizen delivering domestic
waste from his own dwelling, hauler classification 13 in spaces 17
and J8 was used.  Dwellings included living units and asso-
ciated yards. If a private citizen delivered other than domes-
tic waste,  it was necessary to select one of the other code
numbers as appropriate hauler classification.

ITEM NO.  7. CONDITION OF MATERIAL   The unusual
condition of waste delivered to the disposal facility was
recorded in space 29.  For example, in most wrecking jobs
the  refuse  is usually  piled in dump trucks with a  clam shell
or front end  loader.  The engineer who evaluated the survey
sheets took  this into account; however, if a truck load of
waste from a wrecking job was hand loaded allowing much
more than  the usual amount to be loaded in the  truck, a very
dense condition was indicated by placing a  "1" in space 29.
Similarly,  if a load of large cardboard boxes was loose and
not  in any way crushed or packed, a very  loose condition was
indicated by  placing a "2" in space 29.  Normally, no numbers
appear in space 29.  It was used only for the junus_ual_ condi-
tion.

ITEM NO.  8. BULKY    Bulky material was indicated by
recording the number "1" in space 30.  Material not bulky
was indicated by leaving space 30 blank.   Bulky material in-
cludes items larger than or  as large as a  desk or refrigera-
tor,  and pieces greater than 12' long other than a simple
2 x  4  or easily broken items.  In general,  a bulky item was
one that could not easily be crushed  or broken with a small
farm tractor.

ITEM NO.  9. SIZE OF LOAD   The size of load  or volume
was recorded in  one  of three ways.

The first way was to indicate the size  of load by  recording
the  size of vehicle cargo space in cubic yards and percent
to which it was filled.  For example, a dump truck with
a 5  CY capacity box filled half full of tin cans was recorded
as 5 CY x 50% full.   The same truck with tree  limbs piled
higher than the side of  the 5 CY  box was recorded as 5 CY x
120% full.

The second way was  to indicate the size of load by recording
the  length, width, and height of the vehicle box or cargo
space, in feet and percent to which the vehicle was filled.
For example, a pick-up truck with a box 8' long x 4' wide
x 4' high filled one-half full of tin cans was recorded as
8' Jong x 4' wide  x 4' high x 50% full.  CY was  left blank.

                          11-28

-------
The third way was to indicate the size of load by measuring the
length, width, and height of the actual cargo in feet.  For ex-
ample, a flat bed trxick might have a load of scrap concrete blocks
piled an average of 8' long x 4'  wide x 2' high; or an automobile
with a basket of grass clippings in the trunk was described as a
pile 2" long x 2' wide x 1' high.   Since this method indicated size
of cargo and not size of vehicle, the % full was left blank.

ITEM NO. 10.   WEIGHT   The weight of the load was recorded in
spaces 35, 36,  37 and 38,  when provision was made for weighing
of the vehicle.   The weight was written  in multiples of 10.  For ex-
ample, a load weighing 10, 000  Ibs.  was recorded as 1, 000.

ITEM NO. 11.   ADDRESS  OF SOURCE   The address from which
the source of waste originated was recorded in the blanks provided.
For example, if a contractor were wrecking a hotel building in the
3900 block on Farnam Street, "39th and Farnam, Omaha'' was re-
corded.  For city refuse vehicles, the approximate center of the
route was indicated.

ITEM NO. 12.   TYPE OF MATERIAL   The type of material being
delivered was indicated by recording one or more  of the types  of
material listed in one or more  of the material spaces provided.  If
a load was mixed and had a high percentage of some materials and
a low percentage of others, a rough approximation  of the percent-
ages was recorded.  For example, a load of bricks from a wrecking
job with some wood would have  been recorded as follows:

                        TYPE  OF MATERIAL

39


Mat


1.
2.
'1
40
1
c
41
9

42
0
Demolition
Demolition
Mat
43

'1
44
2
- Mixed,
- Mixed,
0
/
45
1

46
0
Mat'l
47 48

% Mat'l %
49 50 51 52 53 54

Non- Combust.
Combust.
In the case of a typical load from a City Refuse Packer Truck, "40.
Garbage and Kitchen Waste,  Domestic",  or "42.  Mixed Trash and
Refuse Including Garbage" was indicated,  but no attempt was made to
evaluate the percentage of any of the materials in the load.  "6. Con-
struction Mixed" indicated any scrap materials or other materials
derived from the construction industry which did not fall into other
specific  categories listed.  "Ashes and Cinders" designated the normal
residue and clinkers from burning of coal and other  combustibles  as
opposed  to "Fly Ash" which designated very fine, light material.

                            11-29

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         ITEM NO. 13.  COORDINATE, GOVERNMENT SUBDIVISION,  AND
         GEOGRAPHIC AREA  The coordinate of the source of waste, the
         government subdivision and geographic area were determined in
         the office by the person processing the survey sheets.  No entries
         were made in spaces 55 through 66 by surveillance field personnel.

         A map of the Study Area was divided into 1, 000 foot grids number-
         ing south from a zero grid line (which ran east and west) at Latitude
         42°00'00".  Each  grid line south of this zero grid represented  a
         1, 000' distance.  West Dodge Road in the vicinity of Boys Town is
         approximately 296, 000 ft. south of the zero grid and is referred to
         as S296.

         The other direction in the grid system was numbered west of a zero
         grid line (which ran north and  south) at Longitude 94°00'00".  Each
         grid line west of this zero grid represents  a. I, 000' distance.  Seventy -
         Second Street in Omaha is approximately 556, 000 feet west of the zero
         grid and is referred to as W556.

         The address of the source of a load which is explained above in Item
         No.  11 was found  on a grid map of the Study Area.   This address was
         converted to grid  coordinates and listed in spaces 55  through 60
         using  the closest grid lines both south and west.

         At the same time  the address was  coded  for coordinates, the political
         subdivision was recorded in spaces 6l  through 63.  A listing of the
         political subdivisions which appeared during the survey is  shown in
         Figure 11-11.

         The Study Area was also divided into geographic areas which were
         land masses representing areas 15,000 feet square in the urban areas
         and 25, 000 ft.  square in the rural  areas.  A further discussion per-
         taining to geographic areas is  found in Part III.

The landfill surveys were scheduled to  avoid unusual conditions.  Weeks con-
taining holidays were avoided.  Whenever a holiday fell on or near a weekend
the surveys were delayed beyond the weekend to avoid recording accumulations
due to the holiday.  Similarly,  weather conditions were considered.  Where
rain and wet weather became a possible factor,  the survey in progress was
abandoned and  restarted after the weather and site conditions had improved.
Each  site survey  covered a typical work week free of disruptive conditions.

         2«       Computer Programs

                 ji.     General.  In all of the programs certain terminology
is used which must be understood.   The reader is cautioned to be certain the
right  data is selected and the right conditions and units are used.  The termi-
nology is not difficult or profound; it is tedious.  Reference will be  made to

                                 11-30

-------
computer programs by program designations A, B, C,  D,  E, F, etc.
For example:  Program D, "As Received Quantities of Refuse by Type of
Vehicle and by Geographic Area" was produced in eight variations by sort-
ing the data into eight different groups or combinations.  There was one
sort for each of the seven sites representing one week at each site and one
additional sort which produced the total for all sites.  When  sorted by the
entire week, the totals are per week.  The week may be seasonally adjust-
ed to convert the raw data to a typical week,  but in each case it is labeled
to reflect the true conditions.  There are certain special cases where this
procedure is changed; but in each case the  data is properly marked to re-
flect the true conditions.

Before any programs were run,  all of the data was tested in  specific test
programs to find potential errors.   In total there were eight  sorts for Pro-
gram A through N; one for each survey  site and one for the total of all sites
for a final total of 112 sorts.   All of the data is not reproduced in this re-
port because of the volume of material.  Certain portions  have been repro-
duced where appropriate.  In general, the data reproduced is that showing
the total for all facilities for each program.  The entire data is available
for interested persons.

Not all of the data in all of the sorts was used in the analysis of the problems
peculiar to this Study Area.  In some cases the data was produced for the
benefit of researchers who may have use for the data not previously avail-
able. The various combinations of data in  some cases were  the result of
simply leaving a computer sub-program in a main program,  and acquiring
basic data as a byproduct while obtaining certain required  information.
We have tried to describe  the data,  how and under what conditions it was
gathered, and how it was adjusted,  to make this information  as useful as
possible to others with similar problems.  We have attempted to produce
data and report exactly the source  and conditions both for our use and for
the use of others as it may apply.

The  basic surveillance data for Programs A through N was processed on an
IBM 360 Model 65 Computer with a  256K core storage locations memory.
The  data was established on cards  and then converted to magnetic tape for
processing.

The terms which are common  to several programs are  explained as follows:

                        (1)       Cubic Yards as Received.  These are  the
cubic yards of material appearing in Columns 31-34 of the survey form. They
are not adjusted for seasonal  or compaction factors.  They are adjusted for
Condition of Material as indicated in Column 29 of the survey form.
                                  II-31

-------
                          (2)    Packer Truck Factor,  When material  is
 delivered in a packer truck, the material is precompacted to the extent  that
 the material would have a greater unit weight and greater compaction than if
 delivered loose.   The unit weights and compaction factors  for each material
 were assigned on the basis of loose material.  When material is delivered
 in a packer truck,the unit weight and the  compaction factor are multiplied by
 two.  The weight is therefore, doubled to reflect the true weight in the truck
 contents.  In those programs where volumes are adjusted for compaction, the
 volume in a packer truck is doubled.
                         (3)      Pounds as Received.  The same as
"Cubic Yards as Received" except the volume of each material on each
load was multiplied by the appropriate unit weight for that particular ma-
terial  to convert from cubic yards to pounds.  The unit weights used are
shown in Table II-8.

                         (4)      Vehicles or Vehicles this Hour.  This is
simply a count of the vehicles for the appropriate  unit of time or type  of
vehicle.

                         (5)      Seasonal Factor Adjustment.  A factor
was assigned to each material which would adjust  the amount of material
received during the day or week to the average daily or 7-day rate which
would  be experienced over the entire year.  The factors are shown in  Table
11-23.

                         (6)      Compaction Factor Adjustment.  A factor
was assigned to each material which would adjust  the materiaJ received dur-
ing the day or week to reduce its volume "as received" to the volume which
it would occupy when mixed with other materials and was compacted into a
landfill.  Cover dirt is not included.  See Table 11-23.

                         (^)      Condition of Material.  The unusual con-
dition  of waste delivered  to the  disposal facility was recorded in space 29.
For example, in most wrecking jobs the  refuse is  usually piled in dump
trucks with a clam shell or front end loader.  The Engineer evaluating these
survey sheets has taken this into account when assigning unit weights; a truck
load of waste from a wrecking job was hand loaded allowing much more than
the usual amount to be loaded in the truck,  a very  dense condition was indi-
cated by placing a "1" in  space  29.  Similarly, if a load of large cardboard
boxes  were loose and not  in any way crushed or packed, a very loose condi-
tion was indicated by placing a "2" in space 29.  Normally, no numbers ap-
pear in space 29.  It was  used only for the  unusual condition.
                                     n-32

-------
TABLE II-8.  MATERIALS, SEASONAL FACTORS, COMPACTION
FACTORS AND UNIT WEIGHTS
Material
Code
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
30
31
32
33
35
36
37
38
40
41
42
43
44
45
46
50
51
52
53
54
55
56
57
58
59
60
61
62
63
70
71
72
73
80
Seasonal
Factor
0.6
0.6
0.6
0.6
0.6
0.6
0. 7
0.7
1. 0
0.9
0.9
0.6
0.6
0.8
0.8
0.8
0.8
0. 1
0.6
1.0
1. 5
1. 0
1.0
1. 0
1. 0
1. 0
1.0
0.8
1.0
1. 0
1.0
0.8
2.0
1. 0
1.0
1. 0
0.9
0.9
0.9
0.9
1. 0
1. 0
1. 0
1.0
1. 0
1. 0
1.0
1. 0
1.0
1. 0
1.0
1.0
1.0
1.0
1.0
1. 0
1. 0
1. 0
1.0
1.0
1.0
0.3
Comp.
Factor
0.8
0.7
0.8
0.6
0.7
0. 7
0.9
0.9
0. 5
0.5
0.5
0.4
0. 3
0.5
0. 5
0.4
0.3
0. 1
0.2
0.8
0.6
0.8
0.8
0.8
0. 5
0.2
0. 1
0. 1
0.8
0.8
0.6
0. 5
0. 9
1. 0
1. 0
0. 9
0. 3
0.3
0.2
0.2
0.7
0. 7
0. 7
0.2
0.2
0.2
0.2
0.2
0.9
0.3
0.5
0.9
0.9
0.3
0.2
0.9
0. 1
0.9
0.9
0. 9
0.9
0.6
Unit Weight
(Loose)
2,400
600
2,430
2,430
2, 560
1,620
2,300
2,430
810
675
675
320
270
675
675
320
270
54
218
1, 730
1, 090
1, 730
1,730
600
4,644
400
60
1, 620
1, 300
1, 130
540
950
1,220
2, 160
2,400
1,620
313
313
308
232
810
810
810
185
160
80
80
300
4, 050
1, 350
182
700
1,200
216
540
1, 080
1,620
1, 750
2, 200
1, 600
1,600
950

Material
Demo -Mixed Non- Combustible
Demo-Mixed Combustible
Dirt, Sand or Gravel
Rock
Broken Pavement or Sidewalk
Construction Mixed
Street Sweepings
Catch Basin Cleanings
Wood
Logs 10 inch diameter and greater
Logs and stumps less than 10 inch.
Limbs and leaves chipped
Limbs and leaves not chipped
Elm logs 10-inch diameter and greater
Elm logs less than 10-inch
Elm limbs and leaves chipped
Elm limbs and leaves, not chipped
Brush
Grass and garden trimmings
Paunch manure
Pen sweepings
Other meat packing wastes
Poultry processing wastes
Dead animals
Slag
Tires and rubber products
Plastic
Oils, tars and asphalts - liquid
Beans or grain wastes
Potato processing wastes
Other food processing waste
Fruits and vegetables
Ashes and cinders
Fly ash
Cement industry waste
Other fine particles
Garbage and kitchen waste - Domestic
Garbage and kitchen waste - Commercial
Mixed trash & refuse - incl. garbage
Mixed trash Si refuse - No garbage
Incinerator residue - Domestic
Incinerator residue, comm. & industrial
Incinerator residue, municipal
Paper and cardboard
Cans
Furniture combustible
Furniture
Major appliances
Heavy metal scrap
Light metal scrap
Wood Crates
Glass and bottles
Battery case and automotive
Automobile bodies
Wire
Chemical Waste, dry
Chemical waste, liquid or wet
Sewage Sludge Solids
Sewage grit
Sewage screenings
Sewage grease skimmings
Agricultural waste
                          11-33

-------
                        (8)      Bulky.   Bulky material was indicated
by recording the number "1" in space 30.  Material not bulky was indica-
ted by leaving space 30 blank.  Bulky material includes items as large as
or larger than a desk or refrigerator, and pieces greater than 12' long
other than a simple 2 x 4 or easily broken items.  In general, items that
could not easily be crushed or  broken with a small farm tractor are con-
sidered as bulky.

                        (9)      All pounds as  listed  in Programs A
through N and shown in Tables II-9 through 22 are 100 pounds.  Multiply
all pounds as listed by 100.

                        (10)      Other terms are explained in  the program
description where they are used.

         ]j.        Computer Program A.  "Quantity of Refuse by Disposal
Process and by  Material Classification. "  In this program materials were
sorted by material classification and by potential disposal  process.  Five
potential disposal processes were considered.  Each load was examined by
the computer and  compared to a set of instructions which determined if  that
load could be accepted by the process.  If it could, the load was recorded for
the process.  If it could not, the load was recorded in  the  space next to  that
process marked "To Landfill"  or  "Not for	" as appropriate.   For
example, a load of broken pavement would be accepted at a sanitary landfill
and so recorded.   When considered for incineration,  it would be rejected
and sent to "To  Landfill".   When considered for composting, it  would be re-
jected and sent to "To Landfill. "  As soon as one potential process was  com-
pleted,  the next process was considered.  The load is  included in all five
processes.

The Sanitary Landfill Process  would accept all materials and is the same  "As
Received CY'1 and "As Received Pounds" except the cubic yards have been ad-
justed for compaction and  seasonal variation, and the  pounds have been  adjust-
ed for seasonal  variation only.

The Incineration Process - All loads and each material content  of a load were
checked to determine if the load could be accepted at an incinerator or should
be diverted to a sanitary landfill.   Loads consisting of materials 2,  9,  11,  12,
13, 15 through 33; 40 through 44;  50,  52,  57, 59, 62,  70,  71, 72, 73,  and 80,
would be accepted. Other  loads containing less  than  25%  of the materials not
listed above would be accepted.  All  other loads would be diverted from the in-
cinerator to a sanitary landfill.  On this basis, two sets of data were determined;
ie. ,  "To Incineration" and "To Landfill. "  In each of these two  main classifications
the material is shown in cubic  yards and pounds.  They are adjusted for seasonal
factor and for compaction  factor,  where appropriate.
                                     11-34

-------
The Dry Landfill - All loads and each material content of a load were checked
to ck:lermine if the load could be dumped in a dry landfill site.  This site
would be similar to a sanitary landfill but would be one which would not re-
quire the same degree of care in handling and covering to protect the communi-
ty from rats,  odors, gases,  unsightly refuse and insects.  It could be a gulley
or low area in town where filling was desired.  Material which could not be
dlimped in a dry landfill would be diverted to a sanitary landfill site for disposal.
Loads consisting of materials 1, 3,  4,  5, 7,  8,  10 through 17 and 35, 36 and
37 would be accepted.  All  other loads would be  diverted to a sanitary landfill.
On  this basis,  two sets of data were determined; i.e. "To Dry Landfill" and
"Not to Dry Landfill. " This latter set would be  to Sanitary Landfill.  In each
of these two main classifications,  the material is shown in cubic yards and
pounds.  They are adjusted  for seasonal factor and for compaction factor, where
appropriate.

The Wet  Landfill - All loads and each material content of a load were checked
to determine if the load could be dumped in a wet landfill site.  This site would
be similar to a worked out quarry where there was standing water or any other
site subject to ground water saturation where contamination  of ground water
through leaching could occur. Material which could not be dumped into such a
wet landfill would be diverted to a  sanitary landfill for disposal.  Loads con-
sisting of Materials 1,3,4 and 5 would be accepted.  All other loads would
be diverted to a  sanitary landfill.  On this basis, two sets of data •were deter-
mined; i.e., "To Wet Landfill" and "Not to Wet  Landfill. "  In each of these
two main classifications, the  material is shown  in cubic yards and pounds.
They  are adjusted for seasonal factors and compaction factors  where appro-
priate.

Program A was run for the totals for each facility; and the totals for all fa-
cilities.  The  totals for all facilities are shown in Table  II-9.

         c_.        Computer  Program B.  "As Received" quantities of refuse
by vehicle and by hours of the day.  In this program the "As Received" quanti-
ties are sorted by type of vehicle and by hours of the day.  The program is
self-explanatory except to note that the quantities in both cubic yards and pounds
and the number of vehicles are not adjusted for seasonal or compaction factors.
This is true for all programs A  through N,  except for A,  I, J and K which are
properly noted as being adjusted.

Program B was run for each facility and a total  of all facilities.  The run con-
taining all facilities is shown in  Table 11-10.
                                    H-35

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         _d.        Computer Program C - "As Received"  quantities of refuse
by typo of vehicle and by political subdivision.  This program is the same as
Program B except that the  political subdivision is substituted for hours of the
day.  The political (governmental) subdivision  is found in Columns 6l, 62 and
63 of the  survey form.  The run containing all  facilities is shown in Table
IJ-11.

         e_.        Computer Program D - "As Received" quantities  of refuse
by type of vehicle and by geographic area.  This  program is the same as the
previous  Program C except that the geographic area is substituted for the Po-
litical Subdivision.  The geographic area was calculated by the  computer from
coordinates inserted into the computer program.

The  run containing the total for all facilities  is shown  in Table  11-12.

         f.        Computer Program E - "As Received'1 quantities  of refuse
by type of hauler and by hours of the day.  This program determines  the cubic
yards,  poxmds and number  of vehicles for each individual hauler that  comes
into  a site by  the hours of the day.  The run containing the total for  all sites is
shown in Table 11-13.

         j*.        Computer Program F - "As Received" quantities  of refuse by
type of hauler and by type of vehicle.  This program is the  same as Program E
except that type of vehicle is substituted for hours of the day.   In this program
the "As Received" quantities are sorted by type of hauler and by type of vehicle.
The  totals are the same as  Program E.  The run containing the total  for all
sites is shown in Table 11-14.

         h.        Computer Program G - "As Received" quantities  by type of
hauler and by political subdivision.   This program is the same  as Program F
except that political subdivision is  substituted for the type  of vehicle. This
program determines the "As Received" quantities by type of hauler and by po-
litical (governmental) subdivision found in Columns 6l, 62 and  63 of the survey
form.

The  totals are the same as  the programs E and F.  The run containing the total
for all facilities  is shown in Table 11-15.

         i_.        Computer Program H - "As Received" quantities  of refuse
by type of hauler and by geographic area.  This program is the same as  Pro-
gram G except that the geographic area is substituted  for political subdivisions.
This program determines the "As Received" quantities by the type of hauler and
by geographic area found in Columns  64, 65 and  66.  The run containing the
total for all facilities  is shown in Table II-16.
                                      11-38

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         j_.        Computer Program I  - Quantities of refuse and adjustment
 factors by material classification.  In this program all loads were examined
 and each material in a load was sorted by material classification.  The quan-
 tity of material in each classification was adjusted for seasonal and compaction
 factors for e£ich material,  one  at a time.

 The several  columns of data produced are  explained as follows:

                  (1)     Material Received.   The cubic yards and pounds
 are as received but added is the percent of each material to the total.

                  (2)     Bulky as Received.  Includes items  as large as, or
 larger than,  a desk or refrigerator, and pieces greater than  12' long other
 than a simple 2 x  4  or easily broken items.  In general, it included items that
 could not easily be crushed or broken with a small farm tractor.

                  (3)     Compaction Factor.   The factors used to adjust "as
 received" loose quantities to "compacted in place" quantities.

                  (4)     Compacted C.Y.   These are the "as received" cubic
 yards multiplied by the compaction factor expressed as  C.Y. and as % of total.

                  (5)     Seasonal Adjustments.  The factor used to adjust the
 quantities measured during the survey week to make these quantities  repre-
 sentative of the entire year.  COMP CY is the cubic yards as received and ad-
 justed for compaction factor multiplied by  the  seasonal factor.  The % CY which
 follows CY is the  percentage of this material  to the total after adjustment for
 compacting and seasonal  factor.  The POUNDS and % POUNDS are  "as received"
 quantities adjusted for seasonal factor only.   (Pounds  cannot  be compacted).
 CUBIC YARDS are the "as  received" cubic yards adjusted for seasonal factor
 only.   They  are not compacted.

 Program I was run for the  totals for each facility and  for the totals for all fa-
 cilities.  The program containing the total for all facilities is shown in Table
 11-17.

         k.        Computer Program J.   Quantity of Refuse  and  Adjustments
 by Political Subdivision.  This  program is the same as Program  I except that
 the political  subdivision is. substituted in place of material classification (and
 the factors were not reproduced). In this program each individual  group that
was listed  in Program I was added for the  political subdivision, found in Col-
 umns 61, 62  and 63  of the survey form, and the percent of the total of each
 group was  listed for each political subdivision.

The totals  for Programs  I and J are the same.  The program containing the total
for all facilities is shown in Table 11-18.
                                    11-47

-------
                 L      Computer Program K.   Quantity of Refuse and Ad-
justments by Geographic Area.  This program is the  same as Program J
except that geographic areas were substituted for Political Subdivisions.
The totals for Program K are the same as the totals for Programs I and J.
The program containing the total for all sites as  shown in Table 11-19.

                 m.     Computer Program L -  Centroids  of Refuse by
Mcilerial Classification. This program is primarily for the purpose of
determining the centroids of materials which will be explained below; how-
ever, a summation of volumes and weights was included for convenience.
This summation is the volume and weight of material normally stated in
cubic yards and pounds per week, but in this case,  the volumes and weights
have been converted to  annual quantities.  The volume is acre feet per  year
adjusted for seasonal and compaction factors.  The weight is tons per year
adjusted for seasonal factor only.

Centroids were computed for both south and west coordinates.   They were
computed by dividing the sum of all of the products of coordinates x the load,
by the  sum of the load,  where the load was expressed in both seasonally ad-
justed  cubic yards and seasonally adjusted pounds.
           (Coordinate X CY)               > , Coordinate X Pounds
            	    also        ' 	
                - CY                              .   Pounds

The coordinates are those recorded in columns 55 through 60 of the survey
form.  The cubic yards and pounds are "as received. "

The centroids represent the  single theoretical location of all of the material
within a sort.  This  may be the centroid of a material,  a  site,  or the entire
Study Area, as appropriate.

In the typeout,  the columns which are marked SUM are the summation  of CY  X
Coordinate or TONS X Coordinate as appropriate.  The columns  marked CORD
are the coordinates  of a point on a map.  They represent  the distance south
or west of base lines expressed in feet x 1000.

The program containing the total of all sites  is shown in Table 11-20.

                 n.      Computer Program M - "As Received"  - Quantities
of Refuse by Day of  the Week and by Type of  Vehicle.  In  this program the
"As Received" quantities  are by days  of the week and by type of vehicle.  The
program is completely self-explanatory.  The total is  for the total number of
vehicles,  cubic yards and pounds per day, and the total number of vehicles,
cubic yards and pounds for all days.   The program containing the total for
all facilities is shown in Table 11-21.
                                    11-48

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                                TABLE  H-2O  COMPUTER  PROGRAM  L.
                                             TOTAL  FOR  ALL  FACILITIES
                         CENTROIDS OF  REFUSE  BY MATERIAL  CLASSIFICATION, FOR  ALL  DAYS
                MATERIAL
CODE"        DESCRIPTION
   1  DEMO-MIXED NUN COMBUST
   2  CEMG-.MIXEO  COMflUSTABLE
   3  DIRT SAND OR GRAVEL
   4 " ROCK
   5  BROKEN PAVEMENT OR SIDE  WALK
   6  CONSTRUCTION MIXED
   7  STREET SWEEPINGS
   8  CATCH BASIN CLEANINGS
   9  WOOD
  10  LOGS 10 INCH DIA  I GREATER
  11  LOGS £ STUMPS LESS THAN  10  IN
  12  LIMBS £ LEAVES CHIPPED
  13  LIMBS £ LEAVES NOT CHIPPED
  14  ELM LCGS 10 INCH  DIA  £ GREATER
  15  ELM LOGS LESS THAN 10 INCH
  16  ELM LIMBS £ LEAVES  CHIPPED
  17  ELM LIMBS £ LEAVESt NOT  CHIP
  18  BRUSH
  19  GRASS £ GARDEN TRIMMINGS
  20  PAUNCH MANURE
  21  PEN SWEEPINGS
  22  OTHER MEAT PACKING WASTES
  24  DEAD ANIMALS
  25  SLAG
  26  TIRES £ RUBBER PRODUCTS
  27  PLASTIC
  28  OILS, TARS £ ASPHALTS-L18UIO-
  30  BEANS OR GRAIN WASTES
  32  OTHER FOOD PROCESSING WASTE
  33  FRUITS £ VEGTABLES
  35  ASHES £ CINDERS
  38  CTHER FINE PARTICLES
  40  GARBAGE £ KITCHEN WASTE  -DOH-_
  41  GARBAGE £ KITCHEN WASTE~-COML-
  42  MIXED TRASH £ REFUSE-INCL GARB
  43  MIXEC TRASH £ REFUSE -NO GARB-
  44  INCINERATOR RESIDUE -DOM-
  45  INCINERATOR RESIDUE,COML £
  46  INCINERATOR RESIDUE,MUNICIPAL
  50  PAPER £ CARDBOARD
  51  CANS
  52  FURNITURE COMBUST.
  53  FURNITURE
  54  MAJOR APPLIANCES
  55  HEAVY METAL SCRAP
  56  LIGhT METAL SCRAP
  57  WOOD CRATES
  58  GLASS £ BOTTLES
  59  EATTEKY CASE  £ AUTOMOTIVE
  60  AUTOMOBILE BODIES
  61  WIRE
  62  CHEMICAL WASTE, DRY
  63  CHEMICAL WASTE, LIQ OR  WET
  70  SEWAGt SLUDGE SOLIDS
  71  SEWAGc GRIT
  72  SEWAGE SCREENINGS
  SS	AGRICULTURAL  WASTE

                  TOTALS
ANNUAL
I SEASONALLY
ADJUSTED
COMPACTED
ACRE
FEET
32.02
7.57
17.89
0.64
7.30
16.47
4.73
2.60
4.77
1.83
N 1.26
C.34
5.57
ER 6.97
3.35
2.69
1 9.06
0.25
2.51
1.56
16.30
0.08
0.27
0.89
1.78
1.02
1- C.29
1.15
4.45
C.81
28.83
C.21
1- 12.66
IL- 2.82
tRB 96.83
IB-' 43.75
0.27
;ND 0.13
IL 0.11
61.90
4.23
1.03
2.47
1.50
4.05
" 	 4.67
24.36
2.93
3.05
C.34
C.51
1.05
C.86
1.81
C.61
C.54
0.43
I SOUTH COORDINATES
CUBIC YARDS
TONS
7279.23
5231.52
43841.47
2095.74
21528.27
30746.74
9741.19
5659.14
6229.89
1994.50
1369.74
219.65
4045.45
7587.64
3647.93
1733.89
6576.18
109.54
2206.00
2725.79
23886.16
134.94
165.36
6652.98
2876.31
493.35
3726.76
1504.08
3229.19
1245.37
31524.17
299.05
10651.09
2371.56
120282.81
40941.73
248.51
124.25
100.03
46235.75
2728.77
332.07
795.99
1813.26
14691.95
SUM
32047.
92012.
185019.
8994.
87063.
201892.
45108.
24425.
80052.
30993.
21429.
7475.
156892.
120496.
58116.
58011.
247988.
20774.
102346.
11546.
116731.
861.
2951.
14932.
66860.
79344.
23435.
12193.
31493.
9744.
263903.
1782.
180659.
43440 .
2264245.
1412561.
3115.
1693.
1302.
2153943.
130954.
43142.
103031.
60868.
35453.
COORD
275.
274.
267.
271.
269.
277.
277.
273.
271.
273.
275.
283.
272.
279.
280.
278.
271.
269.
270.
284.
274.
287.
278.
271.
270.
270.
265.
274.
274.
271.
266.
251.
269.
284.
271.
270.
264.
287.
274.
"270.
273.
270.
269.
267.
270.
16936.85 128785. 270.
7153.13
1836.19
3275.98
199.79
1117.58
1020.71
11229.16
2834.65
1201.20
773.76
554.27
360943.
22029.
28400.
10049.
22022.
8554.
59592.
17425.
5817.
5123.
4138.
271.
269.
270.
282.
277.
273.
286.
280.
277.
275.
277.
I
TONS
SUM
38457.
27604.
224795.
10928.
111441.
163533.
51875.
29676.
32421.
10460.
7232.
1196.
21180.
40667.
19614.
9282.
34164.
567.
11442.
14728.
126016.
745.
885.
34672.
14957.
2565.
18983.
7925.
17006.
6496.
160979.
1443.
55122.
12991.
627225.
213204.
1262.
686.
527.
241099.
14309.
1726.
4121.
9310.
76425.
88136.
37345.
9490.
17040.
1085.
5946.
5391.
61706.
15247.
6399.
4099.
2942.
COORD
275.
274.
267.
271.
269.
277.
277.
273.
271.
273.
275.
283.
272.
279.
280.
278.
270.
269.
270.
281.
274.
287.
278.
271.
270.
270.
265.
274.
274.
271.
266.
251.
269.
285.
271.
271.
264.
287.
274.
271.
273.
270.
269.
267.
270.
271. ~
271.
269.
270.
282.
277.
275.
286.
280.
277.
275.
276.
NEST COORDINATES
CUBIC
SUM
64468.
181131.
369581.
17649.
173165.
401271.
87556.
46798.
152014.
60203.
41365.
13694.
3055.69.
230211.
110726.
109678.
489788.
41008.
204138.
22166.
236246.
l£>23.
5550.
2S093.
132733.
151332.
46955.
22917.
59612.
18546.
£24562.
3820.
344805.
86000.
4547006.
2805028.
6357.
3115.
2446.
4268879.
249445.
86785.
202631.
119953.
69465.
251082.
758277.
44468.
55469.
19828.
41384.
17517.
120217.
32697.
10983.
9619.
8150.
YARDS
COORD
553.
540.
533.
532.
535.
550.
537.
522.
514.
530.
530.
519.
531.
532.
533.
626.
534.
531.
538.
546.
555.
541.
524.
528.
536.
515.
531.
515.
518.
515.
52C.
538.
513.
563.
545.
536.
539.
528.
515.
536.
519.
544.
530.
526.
528.
527V
540.
543.
528.
557.
520.
559.
576.
525.
523.
517.
546.
TOMS
SUM
77362.
54339.
449041.
21444.
221677.
325029.
IOC689.
56860.
61567.
20318.
13961.
2191.
41306.
77696.
37370.
17548.
67553.
1119.
22833.
28792.
254965.
1404.
1665.
67553.
29485.
4883.
38033.
14896.
32190.
12264.
31SS94.
3094.
105069.
25655.
1260975.
423969.
2575.
1262.
9S1.
4776PO.
27068.
3471.
8115.
18343.
149265.
171907.
7427d.
19366.
33282.
2141.
11174.
11017.
124438.
28610.
1207.
520.
561.
57(j.
525.
523.
517.
549.
                                        ***** 529746.94  9344J27._Zl\f__2766705.   272. 18517152. 537.  5485408.  538.
                                                         11-50

-------An error occurred while trying to OCR this image.

-------
                 <).      Computer Program N - "As Received quantities of
refuse by day of the week and by type of hauler.  This program is the same
as Program. M except that the type of hauler is substituted for type of ve-
hicle.  The totals are the same as Program M.   The Program containing the
tolal for all facilities  is shown in Table 11-22.

F\	VOLUME,  WEIGHT AND VEHICLE ANALYSIS

         1.       General.   Computer Programs A, B,  E and I are the prin-
cipal  source of information concerning volumes and weights of waste material.
They  indicate when and by whom the materials were delivered, other infor-
mation concerning vehicle types and the relative amount of material disposed
of at the several landfill  sites  surveyed.  This information will be of value  in
making detailed plans for operation of new sanitary landfill sites or transfer
stations.

The following explanations,  of a general nature,  contain items of significance
concerning  the development  of disposal facilities for the Study Area.  From the
large store of basic data, the detailed facts may be obtained for proper plan-
ning and design.

         2.       Comparing the Several Sites for Waste Quantities and Ve-
hu ular Traffic.  Figure  TI-2 shows the percentage by volume  and weight  of
material, and vehicular traffic at each of the  six major landfill sites and one in-
c merator.

This figure graphically illustrates that Meese's Sanitary Landfill receives a
higher tonnage and cubic yard input than any of the other sites.  This is  ex-
plained by the fact that this site receives  practically all of the municipally col-
lected domestic waste from  Omaha and is strategically located in a position
to receive much of Omaha's  commercial and industrial solid waste.

The Council Bluffs Dump site has a higher vehicle  count due to a large number
of pick-up trucks that use this site.  It has  the third and fourth highest per-
centage of cubic yards and tons received, respectively.

Reasons for any unusual  pattern can be found by examining the detailed com-
puter programs.

         3.       Comparing the Several Vehicle Types for Waste Quantities
and Vehicular Traffic.  Figure II-3 shows the percentage by volume and weight
of materials,  and vehicular  traffic for the ten different types of vehicles.   It
might be expected that most of the material going to a  landfill site would be
brought in packer trucks hauling waste from the  residential dwellings and com-
mercial establishments  in the  community. This is  correct.  Such waste is  a
major category and a  major contributor as  shown in the fiture.  The largest
volume is brought in packer  trucks with the  flat bed trucks bringing in the second
largest volume.  The  flat bed trucks are used extensively to haul diseased elm logs
and limbs.

                                      11-52

-------
    CUBIC  VARDS
                                   TONS
                                                            VEHICUES
      DISPOSAL  SITES           OPEN
A  SARPY COUNTY LANDFILL     7Days/Week
B  DOUGLAS COUNTY LANDFILL   6Days/Week
C  MEECE'S SANITARY LANDFILL  6 Days/Week
                                Su n day
D  OMAHA  INCINERATOR          7Days/Week
E  COUNCIL  BLUFFS LANDFILL    5 Days/Week
F  COUNCIL  BLUFFS DUMP        7Days/Week
G  OMAHA  CITY DUMP            5Days/Week
                                      thru
  HOURS
08OO-I700
0800- 1700
0700 - 1800
O8OO - I2OO
OOOO-230O
O8OO-I700
073O -1800
07OO -1600
 for individual sites
For quantities and weights ,see EXHIBITS
and     for the total.
One hundred per cent  equals 38,884 CY/WK;  11,900 TONS/WK; 4439
VEH./WK; as received.
                        COMPARING  THE SEVERAL. SITES
                                           FOR
                    WASTE QUANTITIES  &. VEHICULAR TRAFFIC
                                                          FIGURE TT-2
                               11-53

-------
40-
      CUBIC YARDS
                                  TONS
                                                         VEHICLES
            VEHICLE  TYPES
          A  PACKER TRUCK
          B  DUMP TRUCK
          C  VAN TRUCK
          D  LIGHT  TRAILER
          E  HEAVY TRAILER OR SEMI TRAILER
          F  FLAT BED TRUCK OR STAKE TRUCK
          G  PICKUP TRUCK
          H  AUTO OR STATION WAGON
          I   TRANSFER TRAILER
          J  OTHER
                           COMPARING THE VEHICLE TYPES
                                           FOR
                     WASTE QUANTITIES a VEHICULAR TRAFFIC
                              11-54
                                                         FIGURE H-3

-------
The highest tonnage was brought in packer trucks.  These trucks delivered
approximately 33"/i of the total.  Packer trucks were also the second high-
est in number  of vehicles.

The dump truck is the second highest in tonnage delivered, fourth in cubic
yards and third in the number of vehicles.

The largest traffic is in pick-up trucks.  These vehicles deliver approxi-
mately  11% of  the tonnage,  approximately 16% of the volume, and represent
approximately 30% of the Iraffic.   This volume is "As Received'1 and usually
is very loose.

The automobile accounts for  approximately 15% of the vehicle traffic but
only for 1% of  the volume and 0. 5% of the tonnage received.  The automo-
bile adds to the traffic but deposits only a small amount of material.   In an-
other part  of the report, it is recommended that automobiles be excluded
from the main fill areas, but be allowed to dispose of their refuse in a  special
area without being charged for doing so, since they contribute very little to
the volume and tonnage.

         4.        Comparing the Several Hauler Types for Waste Quantities
arid Vehicular  Traffic.   Figure 11-4 shows the percentage by volume and weight
of materials and vehicular traffic for the thirteen different types of haulers.

In this figure the largest volume and tonnage appears to be the  Commercial
Hauler,  Domestic Route Type D.   The figure accurately shows what the com-
puter program reported, however,  there is an error in this  particular data.
The survey technicians sometimes used Type D when Public Domestic Type I
should have been used.  Specifically,  the Contractor collecting Omaha's
domestic refuse was classed as Type D in lieu of Type I.  He is a commer-
cial collector in one  sense of the term, but in this case, he was working in
lieu of the municipality's own forces and as such should have been classed
as Type I.   It is possible and proper to combine the results of Types D and I.
To use this  data,  consider the sum of Types D and I as the total domestic  ref-
use which was  collected by Public  and Commercial Domestic Haulers.

In this figure,  the Private Citizen  Domestic, Type M appears as the high traf-
fic and  relatively  low quantity category.  This  can be accounted for in the  large
number of automobiles which bring small quantities of waste and an even lar-
ger number of  pick-ups bringing relatively small loads,  many of which are
privately owned.

The reason for the extremely low quantity of waste from the general contractor
and wrecking contractor in both volume and tonnage is that the  majority of the
contractors have their own disposal sites, as explained in Section B of this
Part II.
                                     H-55

-------
40-
       CU Bl C  YA RDS
                                        TO N S
                                                                  VEHICLES
      HAULER  TYPE
    A CONTRACTOR, GENERAL (General construction wastes)
    B CONTRACTOR, WRECKING (General demolition wastes)
    C ELM TREE  REMOVAL (Diseased elm trees removed)
    D COMMERCIAL HAULER, DOMESTIC  ROUTE (Commercial route system, residential portion)
    E COMMERCIAL HAULER, COMMERCIAL ROUTE (Commercial route system, commercial portion)
    F COMMERCIAL HAULER, INDUSTRIAL ROUTE (Commercial route system, industrial portion)
   G COMMERCIAL SINGLE SOURCE (Private  single source, commercial establishments)
   H INDUSTRIAL SINGLE SOURCE(Private single source, industrial establishments)
    I  PUBLIC DOMESTIC (Public source, domestic waste)
    J  PUBLIC COMMERCIAL  (Public source, commercial waste)
    K PUBLIC INDUSTRIAL (Public source, industrial waste)
    L OTHER PUBLIC VEHICLE (Any other Government Vehicle)
   M PRIVATE CITIZEN DOMESTIC (Private  citizen, domestic waste)
                                COMPARING  THE  HAULER  TYPES
                                                   FOR
                           WASTE QUANTITIES a  VEHICULAR TRAFFIC
                                                                  Fl GURE
                                  11-56

-------
         S.       Comparing the Seven Days of the Week for Wast ,• Quantities
 .tnd  Vehicular Traffic,  figure TI-5 shows that the quantities and traffic are
 reasonably uniform from Monday through Friday with Tuesday being slightly
 greater.  Saturday shows a reduced volume and tonnage but increased vehicu-
 lar count.   This  can be explained by the reduced commercial,  industrial and
 municipal  activity and an increase in  personal hauling.   Reference to the de-
 tailed data shows that a high percentage of the Saturday and Sunday traffic is
 pickups and automobiles.  This is particularly true at the  Council Bluffs dump
 site  which is open all day Saturday and Sunday.

 The  recommended new sites are planned for a 6-day week, Monday through
 Saturday.  It is contemplated that  special facilities will be provided for auto-
 mobiles -which will be available 24-hours  per day, seven days  per week.

         6.      Comparing the Hours of the Day for Waste Quantities  and
 Vehicular  Traffic.   Figure II-6 shows that the peak hour for volume, tonnage
 and vehicle count is 1100 hours (11:00 A.M.).  The second highest peak is
 1500 hours (3:00 P.M.).

 The quantity and traffic are low prior to 0700 and after 1800 hours.  Some  of
 the sites are not open before 0800 and close before 1800 hours; however, this
 chart indicates no large demand for service  during these early and late hours.
 Notice there is no large backlog waiting at 0800.  If there was such a back-
 log,  there  probably would be a dropback between 0800 and 0900. Instead,
 there is a  continuing increase until 1100.  The rate slacks at the peak of 1100
 and drops  down at 1200 hours and increases again to the second highest peak
 at 1500 hours.  Then the rate slackens continuously to  1800 hours.

 Our recommended hours for landfill sites are from 0800 to 1800 hours.  Spe-
 cial arrangements can be made for haulers inconvenienced by  this schedule.

         7.      Comparing the Hours of the Day and the  Vehicular Count
/or (he Several Types of Vehicles.  Figure II- 7 shows the  traffic pattern
 throughout the day by  vehicle type.

 This figure can be very useful in the design of landfill facilities and in making
 policy  decisions.  When providing scale capacity and other functions, it is neces-
 sary to know the  magnitude and timing of  peak operations and the type of hauler
 and vehicle involved.  For example,  it can be seen that automobiles, with 15%
 of the  traffic, have a peak rate of arrival at  1500 hours.  This peak coincides
with  a  total traffic peak shown in Figure  II-6. Anything which  reduces  the
number of  automobiles at this  time, significantly reduces the peak traffic.  We
have recommended automobiles be provided special facilities which will eli-
minate them from Ihe traffic usmg the scales and other critical facilities.  They
would also have a significant effect on the 1 100 hour peak.
                                      n-57

-------
25
     CUBIC YARDS


          M  MONDAY
          T  TUESDAY
          W  WEDNESDAY
          T  THURSDAY
          F  FRIDAY
          S  SATURDAY
          S  SUNDAY
       TO N S

DAILY   TRAFFIC
                                                            VEH ICL.ES
                     COMPARING THE SEVEN  DAVS OF THE WEEK
                                            FOR
                      WASTE QUANTITIES & VEHICUUAR TRAFFIC
                               11-58
                                                           FIGURE H-5

-------
I-
0
h
h
z
U)
0
IT
til
Q.
              8  IO 12 14 16 18 2O -22 24
                                                       18 2O 22 24
       (0000 HRS  TO  2300 HRS)


          CUBIC YARDS
(OOOOHRS  TO 2300HRS)


        TONS
O 2 4 6  8 10 12 14 tS  18 2Q 22 24


  {OOOOHRS TO  2300HRS)


        VEHICLES
                                    HOURLY   TRAFFIC
                              COMPARING  THE HOURS  OF THE  DAY

                                                       FOR

                            WASTE QUANTITIES » VEHICULAR TRAFFIC
                                      11-59
                                                                          FIGURE
                                                                                       -6

-------
   VEHICLE
                                                   HOURS
TOTALS 81 TYPES -0 Ol °° 030° os-oo 07.00 0900 u oo 13-00 15-00 1700 19-00 2100 23:00
781 '5
PACKER TRUCKS 10
17.6% 5
0
IS
674 ,0
DUMP TRUCKS
15.2% 5
0
20
299 '5
VAN TRUCKS >°
6.8% 5
0
(D 20
III^'5
LIGHT TRAILERS * 'o
2.5% £ 9
1- o
20
48 ^'5
HEAVY TRAILERS 0 10
1.1% 5
1- o
2 20
U ,,
508 o
FLATBED TRUCKS 10
11.5% o: 5
UJ o
0. 2°
1339 l5
PICKUP TRUCKS I0
30.2% 5
0
20
671 15
AUTOMOBILES '°
15% 5
TRANSFER VEHICLE
.02% 5
(Less than 1% not shown) o
25
10 2°
OTHER u
.23% I0
(Less than 1% not shown)
5
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                  00:00   02 00   0-4100

TOTAL FOR ALL VEHICLES 4439
                                     os:oo   08:oo
:oo   12:00   14.00   16:00   ie:oo   '2000   22:00
HOURS
                                                       COMPARING THE
                                      HOURS  OF  THE  DAV  & VEHICULAR  COUNT
                                                                FOR
                                               THE TYPES  OF  VEHICLES
                                           11-60
                                                                          FIGURE H-7

-------
In the case of pick-up trucks,  representing 30% of the traffic, a peak at  1100
and again at  1500 hours also coincides with the total traffic peaks.  In fact,
the automobiles and pick-up are largely responsible for these two peaks.  It
wmdd be possible to establish a flat rate fee for pick-up trucks or pick-up
I rucks without side boards.  If this were done, these trucks would not have to
be weighed,  thus reducing scale congestion.  Of course,  enough pick-ups
should be weighed during non-peak periods  to establish a typical weight for
rec-ord purposes.

Packer  trucks show a peak at noon.  Since these  vehicles represent 17.6%
of Ihe traffic and carry the largest single portion  of the total volume and ton-
nage, their arrival should be planned and facilities provided to prevent a traf-
fic back-up.   They should be  given special consideration for two other reasons
as well.  These are self-unloading vehicles which can be dumped rapidly,  thus
avoiding a prolonged stay in the congested area at the active fill face.  Non-
self-unloading vehicles, by contract, must be unloaded by hand and remain at
the active fill face for a considerably longer time. Packer trucks also usually
carry a multiple man crew.  It is  particularly important to the packer truck
operator to move into the landfill and out again as soon as possible to reduce
unproductive time of idle crew members.
G.
ORIGIN OF LANDFILL WASTES
         1.        Centroids.  Computer Program L determined the centroid
of waste for each material  classification for the  sum of all days for each site
and for all days at all sites.  The centroid is the theoretical point from which
the material originated.  The centroid of waste for each site  surveyed is as
follows:
                                Origin of Wastes
         Site

Sarpy County Sanitary Landfill
Douglas  County Sanitary Landfill
Meese's Sanitary Landfill
Omaha Municipal Incinerator
Council Bluffs  Landfill
Council Bluffs  Dump
Omaha City Dump
                                        Centroid

                                 35th & Edna, Sarpy County
                                 76th &• Pacific,  Omaha
                                 38th & California,  Omaha
                                 20th fc Harney,  Omaha
                                 7th St. & 8th Avenue,  Council Bluffs
                                 7th St. & 2nd Avenue, Council Bluffs
                                 18th &c Cumin g, Omaha
The centroid for the sum of all days and all sites, -which includes all material
brought to the seven sites surveyed, was found to be located near the intersec-
tion of 29th  &. Harney Streets,  Omaha.
                                      H-61

-------
         2.       Geographic Area as Origins of Waste.  The entire Study
Area was divided into many geographic  areas as described in Section E.
The material quantities originating in each of the geographic areas is shown
in Figure III-I.  This information is used in site simulations described in
Parl  III of this report.

         3.       Political  Subdivisions as Origins of Waste.  Computer
Programs C, G and J shown in Table 11-11,  15  and 18  respectively lists the
waste material from each of the political subdivisions which contributed
waste to any of the seven major disposal facilities  surveyed.  These materials
are further  broken down into:  Types of Vehicles; Types of Haulers; and As
Received and Adjusted Quantities.

Table 11-23  is an excerpt from  Table 11-18 showing the "As Received" quanti-
ties and the percentage of these quantities  received from each political sub-
division.  Wastes originating within  the City of Omaha  were approximately
equal to two-thirds of the total.  The sum of those  originating within Omaha,
Council Bluffs  and the unincorporated part of Douglas  County were approxi-
mately equal to 94 percent.
                             TABLE 11-23

       Comparison of Wastes as Received from  Political Sub-Divisions
                           Computer Program J
Political                     Cubic      % of                   % of
Sub-Division                 Yards      Total       Tons      Total
 1.  Omaha                 25,579       65.8
 2.  Ralston                   188         0.5
 3.  Irvington                   55         0. 1
 4.  Bennington                 31         0. 1
 8.  Waterloo                    5         0.0
 9.  Elkhorn                     1         0. 0
11.  Millard                   '339         0.9
12.  Council Bluffs          8,165       21.0
13.  Carter Lake               281         0.7
15.  Crescent                    3         0.0
18.  Lake Manawa               45         0. 1
33.  Bellevue                  146         0.4
34.  SAC                       406         1.0
35.  Papillion                  164         0.4
37.  La Vista                    58         0.2
50.  Douglas County         2,857         7.3
51.  Sarpy Co.                 460         1. 2
52.  Pottawattamie County       81         0. 2

             Totals         38,900      100%
7,






2,







1,


557
43
22
7. 3
0. 5
0. 1
99
536
45
4.2
12
36
149
68
14
187
105
13
63.5
0.4
0.2
0. 1
0.0
0.0
0.8
21.3
0.4
0. 0
0. 1
0.3
1.2
0.6
0. 1
10. 0
0. 9
0. 1
11,891
100%
                                  11-62

-------
H_.	PRESENT QUANTITIES

         1 .        Measured Area.  The total waste measured at the major
disposal facilities, during landfill surveys described in Section E,  are shown
in Table IT-24,  Line a. ,  Columns 11 and  14.  These were taken directly from
(he computer programs and are referred to as this 1968 measured quantity.
In "Line b_. ,  Columns 1 1 and 14,  are shown the estimated additional quantities
of waste which were disposed of on-site,  that would have  been delivered to
these facilities  during  1968,  if more strict regulations and controls concerning
sanitary landfills and air pollution had been in effect and enforced.  These lat-
ter quantities are referred to as  on-site or b_.  Quantities.  The sum of Lines
a., and b_. ,  the measured quantities and on-site quantities,  are the  1968 annual
rate of disposal of solid waste in the "Measured Area" which contributed waste
to the major disposal facilities surveyed.  These totals which appear in Line
1968 of Table 11-24 are equal to 919, 000 cubic yards and 681, 000 tons.

The line b_.  quantities were developed in the  Commercial and Industrial Survey
and other studies described in Sections B, C and D.  They also contain an ad-
justment for materials  disposed of at the  Bellevue Landfill.   The Bellevue pop-
ulation was included in the  Measured Area population but disposed  of material
at their own landfill.   By adding Bellevue quantities into the on-site quantities
in Line b_. ,  their waste and population were included in the measured area.

The measured area can be  described as the urban part of the Study Area and in-
cludes:  Bellevue,  Bennington, Boys Town, Carter Lake,  Council Bluffs,  Cres-
cent, Elkhorn,  Irvington,  La Vista, Millard, Offutt, Omaha, Papillion, Ralston,
Waterloo and eastern Douglas County.   It contains a population of 499, 200 rep-
resenting 94. 4% of the  total population of the Study Area.

The 1968 waste  quantities in the measured area  shown in Table 11-24 have
been divided into four categories: Municipal Wastes,  Domestic Wastes, Com-
mercial and Industrial  Wastes, and Special Tree Wastes.   This was done to
facilitate future projection which is discussed  in Section J.

                  a_.      Municipal Wastes.  The wastes included in this cate-
gory are those which vary directly with the size  of the  city and the number of
people, and are not likely to  have a per capita increase.  People dispose of
certain materials at an increasing rate per person; however, the materials
which are included in this category are likely to  increase  at  a straight  line rate
in direct proportion to  the population.  Included in the Municipal Waste cate-
gory are the materials shown in Table 11-25.   This municipal portion of the  total
waste measured during the landfill surveys is  shown in Table 11-24, Line a:. The
line b_. quantities shown are those representing Bellevue's Municipal waste. The
total estimated  Municipal Waste for the measured area, to be disposed of  at
public  sites in 1968, was 121,400 C. Y.  compacted and seasonally adjusted and
144,300 tons seasonally adjusted.
                                     11-63

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                  b.      Domestic Wastes.  The wastes in this category in-
cludes those types of wastes which normally originate  in the dwelling units
in the Study Area and include  garbage, rubbish and yard waste.  The quanti-
ties shown in Table 11-25 are those of the three hauler classification which
include domestic waste.  The  domestic portion of the total waste measured
during the landfill survey Is shown in Table 11-24,  Line _a.    The additional
material now being disposed of on-site by burning •was estimated in Section C,
and is 6"/< of the measured quantities.  The additional material is included in
(he total materials to be  expected at a sanitary landfill facility and is shown in
Line b_.  The  total estimated domestic wastes for the measured area for  1968
is 397,200 cubic yards and 192,800 tons.

                  £.      Special  Tree Wastes.  This category  of wastes  in-
cludes the quantities of waste •wood which are the result of the Dutch Elm
Disease,  as  discussed in Section D. 3, and includes those material classifi-
cations shown in Table 11-25.  The special tree waste portion of the total waste
quantities measured during the surveillance are shown in Table 11-24, Line a_.
The additional material presently disposed of on-site,  which can be expected at
a public disposal facility in the future is shown in Line b_.  The total estimated
special tree waste for the measured area for  1968  is 159, 600 cubic yards and
119, 100 tons.

                  d.      Commercial and Industrial Waste.  This category of
waste includes all waste not included in the three previous categories of:
Municipal, Domestic and Special Tree Waste.   The quantities measured during
the surveillance is shown in Table 11-25.  The C &: I portion of the total waste
measured during the  landfill survey is shown  in Table  11-24, Line a_. In the
C  Kc I surveys described in Section B,  it was estimated that the 1968 on-site dis-
posal which can be expected to be sent to public disposal facilities was equal
to 18. 8'r/ of the volume and 11. 3"/c of the weight of the present measured quan-
tities and shown in Table 11-24,  Line t>.  The  total  estimated Commercial and
Industrial wastes  for the  measured area for 1968 is 240, 000 cubic yards and
225,200 tons.
                                     11-65

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Material
Class
                TABLE 11-25.  MAJOR CATEGORIES OF WASTE
Per Week                        Per Year
Municipal Waste
1
2
3
4
5
6
7
8
10
11
12
13
70
71
72
73

Hauler
Class
Domestic Waste
4
9
13

Material
Class
C.Y.**
93
235
555
20
226
511
147
81
57
39
11
173
56
19
17
--
2,240



4,470
444
2,019
6,933


Pounds*
380,000
201,200
1, 686,200
80,600
828,000
1, 182, 600
374,700
217,700
76, 700
52, 700
8,400
155,600
109,000
46,200
29,800
--
5, 329, 400



46, 113
5,891
15,319
67,323


Special Tree Waste
14
15
16
17

Commercial and


Total Measured
Municipal Waste
Domestic Waste
216
104
83
281
684
Industrial Waste
C.Y.
per Yr. **
Waste
116,500
360,500
Special Tree Waste 35, 600
Sub -Total

291, 800
140, 300
66, 700
252,900
751, 700

Tons
per Yr.*

138,600
175, 000
19, 600

 Commercial and Industrial Waste
                                                       C.Y.**
                                       Lb.*
                                                       116,500
                                       277, 128,000
                                       (138,600 Tons)
                                                       360,500
                                       350,079,000
                                       (175,000 Tons)
                                                        35,600
                                                      C.Y.
                                                     per Yr. **
                                                       692,700
                                                      -512,600
                                        39, 088, 000
                                       (19, 600 Tons)
                                        Tons
                                      per Yr. *
                          180,100
                                        529,700
-333,200

 196,500
         ^Adjusted for Seasonal Variation
        ##Adjusted for Seasonal Variation and Compaction
                                        11-66

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         2.       The Total Study Area.  The total Study Area has a popu-
lation of 528, 800 as compared to 499, 200 which is the population of the
measured area discussed in preceding paragraph 1.   To obtain present
quantities of the total area, those quantities for the measured area were
increased by the ratio of 528, 800 to 499, 200  and are  shown in Table 11-26.
The 1968 rate of disposal for public disposal facilities for the total Study
Area is equal to a volume of 973, 000 cubic yards, compacted in-place and
seasonally adjusted and a weight of 721, 000 tons seasonally adjusted.

I.        FUTURE QUANTITIES
         1.       General.  Future quantities are estimated based on annual
increased in the present quantities.  The major categories of present waste
and the annual estimated increase  are as follows:

                 Municipal Wastes                        1. 92%
                 Domestic Wastes                           4%
                 Commercial and Industrial                  5%
                 Special Tree Waste                     Fixed Quantity

The annual quantities and accumulated quantities of refuse for 1968 through
1995 for the Measured Area are shown in Table 11-24.

         2.       Municipal Wastes.   The wastes in this category are those
which vary directly as the size of the community, which is estimated to vary
directly with the population.  Therefore, the increase in this category is
estimated to be 1. 92% per year which is the same as the annual increase in
population.  The I. 92% is a straight  line average between  the years I960
and 1995.

         3.       Domestic Waste.  Domestic wastes will  increase directly
as the population increases plus an annual increase in the  per capita rate of
waste.  There are various estimates which predict the rate  of increase in
per capita waste will increase 50% from I960 to 1985.  This is approximately
equal to 2% per year.

Long-term data are difficult to find and when found are difficult to use.  The
conditions under which the data were collected and the type of data included
is  usually unknown.  Two percent per year increase appears reasonable;
therefore, we have used a rate approximately equal  to this amount.

The total increase in annual quantities for Domestic waste is approximately
2% for population increase and approximately 2% for the per capita rate in -
crease for a  total  of 4% per year.
                                     11-67

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         4.       Commercial and Industrial Waste.  We have estimated
these wastes will increase at a rate which is equal to 5% per year.

         5.       Special Tree Waste.  In the special study of diseased tree
waste discussed in  Section D,  it was estimated that 306, 984 elm trees would
be removed in the five years after 1968.  These trees contained 595, 549 tons
or 798, 158 CY  of waste.  We have arbitrarily  estimated that the annual rate
of removal would be equal to 20%  of the total each year for 5 years.  On that
basis for each year from 1968 through 1972, we have included 159,600 cubic
yards and 119, 100 tons.

         6.       Total Future Waste Quantities.  The total future waste
quantities for the Measured Area  and Total Study Area,  from the year 1968
to 1995,  are shown in Table 11-24 and Table 11-26 respectively.

By 1995 it is estimated that the annual rate of  disposal of wastes at public
sanitary  landfill facilities will be  1, 621, 000 cubic yards per year, seasonally
adjusted  and compacted in place; and 1, 190, 000 tons, seasonally adjusted.
The accumulation from 1968 to 1995 is equal to 21, 565 acre feet, and
25,611, 000 tons.
                                  11-69

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         PART THREE - SOLID WASTE DISPOSAL FACILITIES

A.	GENERAL .  The disposal of solid waste, as disciissed in this
part of the report is based on the regional approach.  Under this concept
the several communities in the Study Area jointly provide solid waste
disposal facilities for their mutual use  and benefit.    The recommended
•
organizational structure  and  procedures are presented in Part IV of this
report.  Two of the important principles which  support this joint approach
are:  First,  one or  more large disposal facilities, regardless of the type,
can be operated at a unit cost which is less than that resulting from many
small facilities; and second,  large facilities and operations can  attract
and can afford the necessary full time professional management required
to operate the disposal facilities properly.

Solid waste disposal can  be accomplished using any of several methods,
or combination of methods.   These are  discussed in Section F. 4. of
Part I of this report.  The selection of  the most appropriate method or me-
thods depends on the particular  circumstances that prevail at the time and
in the location where the disposal is needed.  For the reasons explained
in I. F. 4.  we have recommended that several Public Sanitary Landfill
facilities be  provided to dispose of most of the  solid waste generated in
the Study Area.

In addition to material  currently being disposed of at public sanitary land-
fills,  many private  commercial and industrial establishments currently
dispose of their own wastes through the use of a variety of disposal methods.
Where these private facilities are properly operated and do not constitute
a hazard to public health, a nuisance or result in  pollution, they should
be permitted to continue.

The Commercial and Industrial Surveys described in Part II, Section B
show  that more than three-fourths of the tonnage and approximately one
half of the  total volume of commercial and industrial •waste produced was
disposed of at private facilities.  Some  of this material is expected to be
diverted to public facilities if more  strict requirements are placed on all
disposal facilities.  Allowance has been made for this diverted  material
when  determining the required  size  of the public disposal facilities.

Much of the commercial  and  industrial  waste which is currently being dis-
posed of in private facilities  consists of inert materials such as slag,  dirt,
sand and rock, broken  concrete, and other inert demolition wastes.  The
proper disposal of materials  of this  type does not require the  careful
handling and expensive  covering necessary at a sanitary landfill site.
This material can often be used as a fill material to reclaim  or  improve
low land or simply deposited in an inexpensive landfill.

Some commercial and industrial waste  is hazardous or difficult  to handle
at public sanitary landfill sites and must be disposed of by the producer
                                  III-l

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at private facilities.  Included in part, in this type of waste are materials
such as:  contaminated or infectious materials from hospitals; drug, in-
secticide and herbicide waste; paint manufacturing wastes; highly inflam-
mable or explosive materials; fine  powders and others.  The producers
of these wastes recognize the hazardous nature of their materials and
either pretreat them to render them harmless  or dispose of them in their
own facilities.

Provisions have been made for the  licensing and control of private disposal
facilities in the recommendations discussed in Part IV of this report.

In the following sections of this Part IH.Public Disposal Facilities are
analyzed and discussed and recommendations are  developed concerning
the public disposal facilities needed to handle the current solid wastes
and future solid wastes to the year  1995.

JB.	RECOMMENDED METHOD OF  DISPOSAL.  The sanitary landfill
method is recommended for the  following reasons:

         1.      Land is available.
         2.      The  method has been proven satisfactory where
                properly operated.
         3.      The  method can meet all health and sanitation
                requirements,  and be aesthetically pleasing.
         4.      The  method is adaptable to varying quantities
                and peak or slack rates.
         5.      The  method is the most  economical.

C^	SELECTING GENERAL AREAS FOR SOLID WASTE DISPOSAL
         FACILITIES.

         1.      General.  Eight general areas were  considered for potential
disposal facilities as shown in Figure III-l.  One site could  be located in
each general area.

The general areas were selected using the following criteria:

                a.     Minimum driving time and distance to site area.
                b_.     Present land use compatible with sanitary land-
                      filling.
                c.     Accessibility to major highways or arterial
                      streets.
                d.     Economical land cost.
                _e._    General topography,  including terrain, ground cover,
drainage, ground water and major  subsurface  conditions.
                _f.     Suitable earth cover available.

         2.      Driving Time and Distance.  The total cost of solid waste
disposal is the sum of the cost to haul the material from the point of
origin to the point of disposal, referred  to as haul  cost, and the cost of

                                    III-2

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 owning and operating the disposal facility, referred to as disposal
 fee.

 To minimize haul cost,  driving time and distance from the origin of
 the solid waste to the  disposal facility must be restricted to minimum
 values compatible with other selection criteria.
 <•
 The eight general areas selected for this  study are conveniently located
 and provide short driving distances and times for the haulers in the areas
 they would serve.

         3.      Land  Use.  Sanitary landfilling is not in itself objectionable
 but it must be  considered as an industrial activity, and as such, its location
 should be based upon this concept.  The eight sites considered in this study
 are located in  undeveloped agricultural areas,  or in industrially zoned areas.

         4.      Accessibility.  An area accessible from highways and major
 arterial streets is necessary for three primary reasons:

                a^.     The haulers of solid waste material need heavy duty
 roads to transport the loads without damaging the road structures.

                b_.     Major streets reduce driving time and haul cost.

                £.     The additional vehicular traffic generated by a landfill
 facility is of no consequence to the normal flow of traffic on major  streets
 which carry thousands of vehicles per day, but it would be a nuisance if
 routed over local streets which carry only a few hundred vehicles  per day.
 The areas considered in this study with one exception (Site 6) are adjacent
 to either highway or major arterials and the  four sites recommended for
 the metropolitan area are now or will be readily accessible from the Interstate
 Highway System.

         5.      Land  Cost.  Land costs should not influence the overall
 selection process to the extent that other selection criteria are sacrificed.
 The most economical piece  of property that satisfies all selection  criteria
 should be selected.  Fortunately,  costs of land in the areas considered for
 this study were not prohibitive, and when amortized over twenty years, re-
 present only about 10% of the total annual cost.

         6.      General Topography.  The topography of a landfill  area should
be such that it  is not detrimental to landfilling operations, nor should the
 landfill create  water pollution problems.  Terrain, ground cover,  surface
 drainage, ground water,  and subsurface  conditions should be analyzed to
make certain the site can be developed and used for filling without undue
expense and without potential water pollution.  Waste material should not
be placed in ground which could be flooded from surface drainage or saturated
 by ahigh ground water table. Further, the  site should be compatible with
heavy earth moving operations since landfilling is much like major earth
moving jobs.

                                   Ill-5

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The desirable topographic features mentioned for landfill areas do not
apply to transfer stations such as  the one considered in this study at Site 4.
A transfer station is a building structure which must be aesthetically pleas-
ing and compatible with its surroundings  as discussed in Section D. 1.

The eight locations  considered in this  study have no known features which
would be detrimental or incompatible with solid waste disposal  operations.

         7.      Earth  for Cover Material.  After solid waste material is
deposited at a sanitary landfill site, it is spread, compacted, and covered
with a layer of earth.  Usually, several layers  of waste are placed one on
top of another until  the land is brought up to the desired elevation.   Finally,
a layer of earth several feet thick, is placed over the entire  filled
area.

A large  portion of the cost  of a sanitary landfill operation is  the movement
and placement of earth cover.  This cover material must be  suitable in
quality  and adequate in quantity for a proper and economical  site operation.
Except  for Site 6, the landfill areas considered in this study  have abundant
quantities of earth suitable for cover material.   Cover material is not re-
quired at a transfer station.

JD,.	SELECTION OF PROPOSED FACILITIES.

         1.      Transfer Stations .  The primary function of a solid waste
transfer station is to provide for the economical transfer of  solid waste
from some central location convenient for waste haulers to a relatively re-
mote sanitary landfill site.  The transfer of the solid waste is effected by
packing  the refuse of many individual haulers into a large transfer trailer
which is then pulled to the  landfill site, emptied, and returned to the transfer
station.

Following is a discussion of the location, design, capacity, cost, and
economics of transfer  stations in relation to  solid waste handling requirements
for the  Metropolitan portion of this Study Area.  It becomes  apparent that
most haulers would find it  more economical to  haul directly  to a sanitary
landfill site than to  pay the additional fee which would be charged for trans-
fer service.

                a_.    Location of Transfer Stations .  Transfer stations
must be located so as to satisfy the two general criteria of convenience
and economy for haulers and compatibility  with adjacent land use.

                      (1)   Convenience and economy as applied to transfer
stations are interdependent and in many ways synonomous.  If it is more
economical for a hauler to use a transfer station rather  than a  sanitary land-
fill site, then the transfer  station is conveniently located.

                                   Ill-6

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 The most economical location for a transfer station from the hauler's
 viewpoint would be at the  centroid of solid waste generation, provided that
 location is readily accessible from major streets.  Haul distances would
 bf.  short but haul  time is also a  cost consideration. If short hauls re-
 quire relatively long haul times, then a location may  not be economical
 because of its adverse accessibility.  For a transfer  station to be economi-
 c'al to haulers, it must be less expensive for a hauler to transfer waste to
 the transfer station and pay a transfer fee plus a disposal fee,  then to haul
 directly to a sanitary landfill site and pay only a disposal fee.

 A transfer station could also be inconvenient and uneconomical if a hauler
 incurred delay and expense,  within the confines of the station,  due to
 inadequate facilities or improper design of the facilities.

 Two locations were considered in this study for transfer stations.  One
 station  site at 108th and Maple,  the present location of the Douglas County
 Sanitary Landfill  site, was selected because of its strategic location in
 West Omaha with good access to the Interstate Highway and because there was
 an existing  solid waste disposal facility operating.  It was assumed that the
 transfer station would go into operation when the present  sanitary landfill
 site was filled and closed.  The second station site was at 6th and Seward
 Streets in Omaha, the location of the Municipal Incinerator which has now
 been converted to a city-operated transfer  station.  This  site was selected
 because of its location in an industrially zoned area where large quantities
 of waste are generated.

 Both transfer  site locations were considered with a variety of combinations
 of other facilities using economic simulations which are descrioed in
 Paragraphs 1. e_. and 2 of this Section  D.  They were found to be uneconomical.
 Subsequent investigations  showed that no location would be economical when
 there were  sanitary landfill sites proposed within a reasonable direct hauling
 distance.

                      (2)   Activities at a  solid waste transfer  station  are
 industrial in nature.  As such, these activities should be  conducted in an
 area where they are  compatible  with those in the surrounding area,  and the
 transfer station buildings  and grounds should be aesthetically pleasing in
 order to be  acceptable to the public.  A transfer site  should be located  in an
 area where  the amount of  vehicular traffic and traffic patterns  generated by
 a transfer station will not place  a burden upon streets meant for light duty
 use.

                b.    Design of Transfer Stations.  The preliminary design
 of a transfer station includes site planning, building arrangement,  and  transfer
 capacity. A preliminary site plan and building arrangement is shown in Figure
 I1I-2.

                      (1)   The  site planning consists of  determining land
 requirements, landscaping,  set-backs and site screening requirements,
and determining pavement geometry and grades to serve the 2-level transfer
 structure.
                                   Ill-7

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'SITE PLAN
FLOOR PLAN'
       1 ELEVATION
                            TRANSFER STATION
                                            FIGURE m-2
                      III-8

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                      (2)    The building arrangement is made to provide
for the efficient flow of traffic within the building and transfer of  solid
waste from incoming vehicles to the transfer trailer.

                      (3)    The capacity of a transfer station involves the two
elements of  vehicle capacity and refuse transfer capacity.
  •
Vehicle capacity refers to the ability of the  station to handle the number  of
vehicles arriving and leaving  during the station's peak time of use.  This
capacity is provided by proper design of traffic patterns; by providing for
an adequate number of unloading stalls, and by providing for a vehicle
weighing system which will  perform its function efficiently and without
delays.  Traffic flow would  be improved by eliminating from that flow the
relatively large number of automobiles that would use a transfer  station.
This is accomplished by providing  special facilities for automobiles as seen
in Figure III-2.  The required number  of unloading  stalls within the transfer
structure and the adequacy  of a particular weighing system are determined by
computation utilizing the survey quantity and vehicular data shown in Figures
II-9 through 11-22, and the computer printout for the economic site simula-
tions.

The transfer capacity of a transfer station is determined by the capacity
of its least efficient element.  Assuming that the vehicle capacity of the
station is adequate, then the transfer capacity may be limited by the  storage
capacity, the stationary packer system, the labor force, or the number of
transfer vehicles available.   These elements must all be examined separately
and in total in order to provide capacities compatible with the projected use
of the  facility.

               c.    Cost of Transfer. If a  transfer station is to  be self-
supporting, a transfer fee must be  established that will provide enough
revenue to cover the total annual cost of the station.   The cost shown in
Table III-l and the following paragraph^., is for the  Phase I construction
and operation of a transfer station at Site No. 4, which was the most
economical station considered.  In  this example refuse is transferred to
Site No  5, which is the nearest and most economical site for transfer
from Site No. 4.

                d..    Annual Cost.  It has been assumed in the cost estimate
that the transfer station will operate  6 days  per week. It is further assumed
that the station will transfer 420 tons of refuse per day or 131, 000 tons per
year.   To determine a transfer fee it is necessary to convert all costs to dollars
per ton.  These costs include  the annual costs of the station operation, annual
costs  of rolling equipment,  running costs of rolling equipment, and truck
driver costs.

         1.      Annual Costs  - Transfer Station Operation

                a.     Construction costs, amortized  over 20  years @ 6%
                      .0872x141,000=                       $12,300
                b.     Stationary equipment costs amortized over  10 years @ 6%
                      . 1358 x 77,000 =                        $10,400
                                   III-9

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                c.    The interest on land @ 6%
                     . 06 x 22, 000 -                          $ 1, 300
                d.    Labor costs assumed  constant           $31,650
                e.    Miscellaneous costs and utility costs     $10, 000
                f.    Annual Costs,  Transfer Station
                     Operation                                        $65,650
                                                                             *

         2.      Annual Costs - Rolling Equipment

                Amortization + Interest                                $16, 800

         3.      The running costs of the rolling equipment have been
                determined in the estimate to be 24£ per mile.  The
                round trip distance  from the transfer station at Site 4
                to Site  5 is 12 miles.

         4.      Truck  drivers are assumed to  receive
                $3. 40 per hour and  will transfer refuse at the rate of
                20 tons per trip with each trip requiring 45 minutes.

         5.      The transfer fee is  determined as follows:

                a.    Station Operation
                     $65,650/Yr. -s- 131, 000 Ton/Yr.  =     50.2^/Ton
                b.    Rolling Equipment
                     $l6,800/Yr. -:- 131, 000 Ton/Yr. =      12.8^/Ton
                c.    Running Costs
                     24^/Mi x 12 Mi/Trip  -:- 20 Tons/Trip =  14. 4$/Ton
                d.    Driver Costs
                     $3.40/Hr. x-i^-Hr/Trip  -:- 20 Ton/Trip = 12. 8^/Ton
                e.     Overhead and Contingencies @ 20%    =   17. 8^/Ton
                f.     Total Transfer  Cost                  =   $1.08/Ton
                e_.     Transfer Station Economics.  The transfer fee of $1. 08
per ton was used in the site simulations to determine if the transfer station
would receive the refuse needed to produce the revenue required to make the
station self-supporting.  Site  simulations  are further explained and discussed
in the following Paragraph D. 2.

The  simulations were done by computer program.  Briefly, computer inputs
were unit costs,  haul times and distances.  The computer print-out showed
total costs and site use.
                                   Ill-10

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TABLE IIJ-1.  TRANSFER STATION - BASIC DATA FOR COST ESTIMATE
A.
*
B.
C.
D.
E.

PHASE I - STRUCTURE & SITE DEVELOPMENT
1. Main Structure
2. Lower Structure
3. Overhead Doors
4. Mechanical & Electrical
5. Excavation &c Backfill
Sub-Total Construction
6. Initial Site Development
a. Utilities
b. Fencing
c. Grading
d. Landscaping
e. Paving
f . Area Lighting
$39, 000
27, 200
4,800
12, 000
2, 000
5, 000
5, 000
2, 000
3, 000
15, 300
2, 000
Sub-Total Site Development
7. Overhead &c Contingencies
8. Total Cost Construction & Site Development
STATIONARY EQUIPMENT COSTS
1. Packer System
2. Scale System
3. O. H. & Contingencies
4. Total Cost - Stationary Equipment
LAND COSTS
1. 4. 6 Ac C'i) $4, 000/Ac.
2. O.H. & Contingencies
3. Total Cost - Land
TRANSFER STATION LABOR COSTS
1. 3 Men (40 Hr. Wk. )@$6, 000/Yr.
2. Fringe Benefits 4 17% +
3. Subtotal
4. 60 Hr. Wk. , Increase 50% +
Total Labor Costs
ROLLING EQUIPMENT COSTS
1. Tractors
a. 2 Tractors w/o Tires
b. 20 Tires
c. Subtotal
d. Salvage (6 Yrs. )
e. Subtotal
f. Amortization, 6 yr. @ 6% (.203) =
g. Interest on Salvage 6%
Annual Amortization + Interest
$30, 000
34, 000
13, 000
$18,400
3,600
$18, 000
3, 100
21, 100
10, 550
$28, 000
2, 400
30, 400
6, 100
24, 300
4, 940
360'

$85, 000
$32, 300
23, 700
$141, 000
$77, 000
$22, 000
$31,650
$ 5, 300
                               III-11

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TABLE III-l.
 TRANSFER STATION - BASIC DATA FOR COST ESTIMATE
    (Cont'd)
       ROLLING EQUIPMENT COSTS (Cont'd)
2. Transfer Trailers
a. 3 Trailers w/o Tires
b. 24 Tires
c. Subtotal
d. Salvage (6 yr. )
e. Subtotal
f. Amortization, 6 yr. @ 6% (.203)
g. Interest on Salvage
Annual Amortization -f Interest
3. Total Annual Amortization + Interest,
Rolling Equipment
$63, 000
2,880
$65,880
- 13, 180
$52, 700
10, 700
800

$11, 500
$16,800
       RUNNING COSTS - ROLLING EQUIPMENT
       1.      Tires
              a.    Tractors $2,400 -:- 30,000 Mi.
              b.    Trailers $2,880-- 60, 000 Mi.
       2.      Fuel
                   $0. 15/Gal. @ 5 mpg  =
       3.      Maintenance and Repair
              a.    Tractor
              b.    Trailer
       4.      Total Running Costs
              a.    Tractor
                    Tires
                    Fuel
                    M&R
              b.    Trailer
                    Tires
                    M&R
              c.    Tire Hazard
       TRUCK DRIVER COST
       1
       2.
       3.
Time per round trip
Tons per round trip
Rate per hour
                                            0. 08/Mi.
                                            0. 05/Mi.

                                            0. 03/Mi.

                                            0. 03/Mi.
                                            0. 02/Mi.
                                            0. 08/Mi.
                                            0. 03/Mi.
                                            0. 03/Mi.

                                            0. 05/Mi.
                                            0. 02/Mi.
                                            0. 03/Mi.
                                           $0. 24/Mi.
   45 Min.
   20 Tons
$3. 40
                                 IH-12

-------
The 6 simulations which included the transfer station at Site 4 are repro-
duced in Table III-2.  Included in the disposal fee in the first five  simula-
tions is the transfer fee of"$1.08 per ton.  The quantity of refuse received
al the transfer station in these 5 simulations varies from 655 tons/week to
786 tons/week.   For a  6-day work week this represents from 109 to 131
tons per day which is well below the 420 tons per day necessary to make
tHe station self supporting.

In the 6th simulation, the  transfer fee was eliminated to determine what
quantities the station would receive if it were free.   In that situation, refuse
at (he rate of 6130 tons/week or 1020 tons/day would arrive at the transfer
station.  The subsidy required to transfer this refuse is approximately $1.08
x 6130 = $6, 620 per week.  This cost was included in the "Disposal Cost"
and "Total Community  Cost" in the Table in  order to determine actual costs
and properly rank the simulation.

It was apparent that the transfer station was not  economically feasible even
under what were  considered to be minimum design standards and operating
conditions.  A higher fee would further reduce the refuse and revenue re-
ceived, and a. fee set low enough to make  the transfer station economically
attractive to its users would  require subsidy.  A station designed to lower
standards is not  recommended.

The primary cause of the adverse economics of transfer stations in this
Metropolitan Area is the short direct haul to relatively
close sanitary landfill facilities.

         2.      Economic Simulations of  Potential Sanitary Landfill Sites.

                a_.    General. The purpose of the economic site  simulations
was to aid in the  selection of one or more sanitary landfill sites  from the 7
potential sites considered in the Metropolitan area.   The simulations were
accomplished with the aid  of a computer program which used waste quan-
tities, site location, and cost data input to compare  the economics of various
combinations  of the  7 potential sites.

The 7 potential site  locations shown in Figure III-1 are described as to their
general location  and numbered for simulation purposes as follows:
                Site 1      Vicinity of 1-80 & Hwy.  50, Sarpy Co.
                Site 2      Existing landfill east of the Mormon Bridge
                           Pottawattamie Co.
                Site 3      Vicinity of 120th & Fort Streets,  Douglas Co.
                Site 4      Omaha incinerator/transfer station
                Site 5      West of Lake Manawa, Pottawattamie  Co.
                Site 6      Vicinity of 60th & Harrison, Douglas Co.
                Site 7      North of Dodge Park,  Douglas Co.


                                   IE-13

-------An error occurred while trying to OCR this image.

-------
General site locations were selected and examined if they appeared to be
convenient for large numbers of people now and in the future.  If it was found
that a location satisfied the selection criteria of convenience,  accessibility,
zoning,  economy,  general topography, and cover dirt availability , it was
used in the site sumulations.
 It is not practical for even a large  computer to develop all the possibilities
 inherent, to this type of simulation and for this reason certain assumptions
were made and limitations set.  The simulations were purely economic.  It
was assumed that each hauler prefers to dispose of his refuse in the least
 costly manner by taking the quickest route to the landfill, that he,  in fact,
 knows the  quickest route,  and that  he intends to make a direct round trip  for
 (he sole purpose of disposing of tV-e refuse.  It was judged that fewer than
two landfill sites would not satisfy  community needs and that more than five
 sites would not be feasible.   Also,  it was  obvious by inspection of the map
 (Figure III-l) showing the potential site  locations,  that certain site combina-
 tions were not reasonable.  These  practical considerations eliminated most
 of the several hundred theoretical  site combinations resulting  from the seven
 potential sites and made the  simulation process a manageable  and very useful
tool.

                b_.    Computer Input.   Quantity input data were obtained from
the landfill surveys described in Part II.  The particular program used in the
 site simulation  process was  Program D, shown in Table 11-12, which gives
total quantities  for all facilities in  terms of type of vehicle by  geographic
area.  Specifically, the program supplied waste quantities in tons and  cubic
yards,  types and numbers o'f vehicles hauling these quantities,  and the  geo-
graphic areas from which the waste was hauled.  This program supplied otheruse-
ful information  but was primarily designed to supply the data required  for the
site simulation  process.

Computer input for each site location was the haul time and distance from the
center of each geographic area, to  each potential landfill site.   Distances were
determined from maps and times were  computed on the basis of 4 minutes per
mile (15 mph) for local streets, 2.4 minutes per mile  (25 mph) for arterial
streets, and 1.2 minutes per mile  (50 mph) for highways.  Where there -was a
choice of roxites by either, the shortest time or shortest distance, the  shortest
time was selected.

Cost data input  included disposal fees,  transfer fees,  toll bridge fees, and
unit haul costs.  With prior  knowledge of landfill costs in this  and other areas,
disposal fees were set at $1. 25 per ton for publicly operated sites and  at $1.80
per ton for  privately operated sites. These fees were assumed to provide for
the cost of all labor, equipment,  management,  and site development incidental
to a properly operated sanitary landfill.   In addition to the set  disposal fee,  a
minimum fee of $1. 00 was established for all vehicles except automobiles and
station wagons which would be permitted to use the facilities free of charge.

                                     Ill-15

-------
When transfer stations were considered in the  simulations the transfer fee
was added to and considered part of the disposal fee.  Transfer fees were
determined by computation and were discussed in the portion of this report
pertaining to Transfer Stations.  Round trip toll fees were included for those
vehicles using the Mormon Bridge and varied from $0. 70 for automobiles to
$2. 00 for heavy trailers.  Unit haul costs consisted of vehicle running cost
per mile and vehicle operating cost per minute.  Running cost per mile inclu-
ded fuel,  oil,  tires, and maintenance.  This  cost varied from 6£  per mile for
automobiles to 24^ per mile for transfer vehicles. Operating cost per minute
included wages, amortization,  interest,  and  insurance.   This cost varied from
(•>. 5^ per minute for automobiles to 14. 7£ per minute for  transfer  vehicles.  The
simulation program multiplied these unit haul costs for each vehicle by the dis-
tance and time from the  geometric center of each geographic area to each site,
and then determined minimum total cost of hauling and disposing  of waste for
each vehicle.

In sumulations which included Site 4,  it was always considered to be a Trans-
fer Station.  Sites 2 and 6 were the only  sites considered for both public or
priveite  operation.  Site 2  is now a privately operated  sanitary landfill and Site
6 is presently being considered for operation by private interests.  The  other
5 sites were considered for public operation  only.

It was assumed for  simulation purposes  that  any number  of sites  could be op-
erated for the fees used in the simulations.  This, of  course, is not true and
adjustments were made after the  simulations indicated which combinations  of
sites should be considered for further  comparison and after the cost estimates
were developed.

               £.    Computer Output.  Approximately one hundred simulated
site combinations were processed.  Table III-3 shows the results of 28 key
simulations ranked in ascending order of "Total  Community Cost" per week.
All quantities  and costs are for an average week; that is, the measured quanti-
ties of solid waste were seasonally adjusted to reflect average weekly quanti-
ties.  The cost of hauling  the solid waste generated during an average week
arid the  cost of disposing  of that waste  by sanitary landfilling make up  the
"Total Community Cost. "

In most of the simulations, haul cost and disposal cost are approximately
equal in magnitude - making each a significant part of the total cost.   Adverse
haul conditions and/or a higher disposal fee would necessarily make a parti-
cular simulation  rank higher  than otherwise.  For example, when only 2 fa-
cilities  are  simulated, many haulers must travel long distances and haul costs
increase significantly as  seen in Simulation No.  92, Rank No. 17.  Also com-
pare the simulations ranked 5 and 10 which contain the same four sites.   Simulation
No. 52, Rank No. 5, has Sites 1, 2, 3 and 5  with equal disposal fees of $1. 25 per
                                     III-16

-------
TABLE  m-3
ECONOMIC   SITE   SIMULATIONS
                    (HANKED IN ASCENDING ORDER
                    OF "TOTAL COMUNITY COST*}
                                                               E OF HOIWON K>DflE, POTTAHATTAHIE CO .  IOWA
                                                               I KITH 1 MAPLE,  DOUfiUS CO. NE8R.
                                                               OHAHt CITY TRANSFER STiTIM,  DWJLAS CO.  KM.
                                                               W OF LIKE MANAMA,  nTTAMTTAMIE CO  IOHA
                                                               MTU 1 HUM I SON, DOUGLAS CO.  NEIR.
                                                               N OF DOD6E Pitt, DOUGLAS CO.  NEU
                                                                   ' WEXLY QUANTITIES ADJUSTED

                                                                    FOR COHTACTIO* AND / II
                                                                    SEASONAL  VARIATIONS
RUI
I.
1.
3
1.
S
6.
'
1.
9.
10
M.
12.
13.
IV.
IS.
IE.
„.
II
19.
20
11
z:
IS.
24
IS
1C.
27.
21.
SIHUUTIOR
MMEI
• 1
too
n
17
SI
CO
w
S3
91
(2
89
90
87
63
65
„
92
48
15
9S
57
16
46
64
33
96
94
35
SITES
2
3
4
5
1
5
3
t
5
7
j
S
2
3
5
3
E
3
S
6
7
2
3
5
3
5
7
2
3
5
3
5
6
7
3
5
6
3
6
7
2
5
3
5
3
5
3
2
3
H
5
5
e
7
3
6
7
2
5
5
e
7
2
3
2
5
e
7
«
•
I
6
DISPOSAL
FEE
t/TON
1 26
1.25
2.33
< 25
I.Z5
1 IS
I 33
1 Z5
1 15
1 15
2.33
1 25
1 IS
I.ZS
I.2S
2.33
1 25
1 25
1 15
1 25
1 25
1.25
2 33
1 25
1 15
1 25
1 15
1 25
1 25
1 25
1.25
1.25
1 25
1.25
I.2S
t 25
1.80
1 IS
1.2*
1 25
1 25
1.80
1 25
1 25
1 IS
1 25
1 25
1.25
I.2S
1 80
1 K
1 25
1.25
1 25
1 25
1 25
1.25
1 80
I 25
1 25
1 25
1 25
1 25
1 25
1 25
1 25
1.25
1 25
1.25
1.25
I.2S
1 25
1.25
1.25
i 80
1 25
1 25
1 25
1.25
I.SO
1 25
t 25
1 25
1.25
1.80
1.25
1.80
1.25
1 10
1 80
C.Y.*
2576
37*3
H43
5858
BIS
29 56
1306
59>0
2283
3765
1307
59*5
2213
IIS
S220
1325
5960
815
2510
293V
6991
6029
IS26
5965
2 IOW
4558
4219
2V39
2580
37HV
6996
815
2356
7110
2439
815
156
5001
7048
3893
704;
2V6
2439
23V9
4558
evts
3766
7115
2439
VS6
sail
70S3
BIS
5395
7110
60?*
70V3
2U8
6206
815
385
2916
6130
307V
V5S8
5SV5
3217
2104
8659
2557
3531
9789
8638
1303
337V
1282
6332
5706
157V
1 1716
9985
3335
52 IV
VI79
7871
5446
5001
8319
ill
* C Y.
SIS,
52.56$
6. 121
22. I9(
(9 BO*)
St. 5V*
17 14*
2B 27$
(9.11*)
5V. 59*
17 14$
6,121
39 19$
(9.95*)
5*. 69V
6.11$
19.37*
22.03*
52. va*
45 26*
(9,95*)
5473*
15 80*
31 12*
31.67*
16.31*
(9 37*
28 II*
52 52$
6 12$
22 19*
S3 38*
18 31*
6. 12*
3 42*
37. 55*
52.91*
26.97*
52 a*
1 BS*
IB 31$
17 6V*
3V 12*
VB 15$
28 27*
53 12*
18 31*
3 V2*
43 S3*
52 95*
6. II*
40.50*
53 38*
45 26*
52 88$
1 87$
U6 58$
53 1Z*
6.12*
2 89*
21 89$
(46 02$)
69 10$
3V. 22$
41.63*
2V 15$
15 80*
65 01*
19 20*
26.51$
73 49*
ev.ast
982$
25 33$
9 62$
47 54*
42.84*
II 82*
88 18*
7V 96*
25. OV,r
39 14*
n-ss
W II*
VO 89$
37.5!*
62 4G*
TORS*
1949
3061
655
4523
702
2380
769
4CO>
1729
3078
770
461 1
1729
702
MM 3
786
4608
702
1951
2363
5172
4791
786
4611
1787
3654
2907
1840
1951
3062
5175
702
2380
5267
1840
702
3926
5215
2969
5119
140
1840
1979
365V
4556
3078
5270
1840
335
4615
S228
702
4219
6267
VS27
5219
142
4918
6270
702
302
2360
4557
2167
3654
4074
2V60
1787
8V67
193V
2722
7V66
6658
937
2593
1015
4656
4518
1157
9031
7633
2555
4499
2614
3075
6008
41 90
3727
6461
$ TONS
19 13*
*.«$)
SO 82*
6.191
23 36*
{7 55$)
52 78$
16.97*
30.21*
7 56*
52.82*
16 97*
6.89$
40.17*
(7 7)*)
52 94"
6 19$
19 15*
23.19$
50 77*
V7.02S
(7 72*)
52,98*
17.54*
36 86*
2B 54$
18 06?
19 15$
3D 05>.
50. M$
6.89$
23 36*
51 70*
18.06'
6 89*
*'?,$
51 28*
21.34*
51 23*
1.37*
IB 06*
19 42$
35 86*
4V 72$
30.22*
51 73*
IB 06*
3.29*
45 40*
51 32*
6 89$
41 41*
51 70*
47 38*
51 23*
1 39*
48 27$
51 73$
6 89*
2 97$
73 16*
(44 73*)
66.98f.
35 86*
39 99*
24 15*
17.54*
63.47*
18.99*
26 72$
73.28$
66 36*
9.20*
2545*
9 96*
45 70*
44 34*
I 1 35*
88 65$
74 92*
25 OBI
VV 16*
ft 1ft
58.97$
41 03$
36 61$
63.42*
HAUL
COST
2423.-
3440.-
1451 -
8508-
131 17 -
766 -
2523 -
2091 -
6786 -
-fl&r
211! -
6801 -
TiS^
766 -
4504 -
2165 -
67B6 -
IV22I -
766 -
2474 -
2473 -
T!^
5472.-
2186.-
T8&Hi
1979 -
7358. -
382} -
1 5340""-"
2474 -
3455 -
-9VJ5.-
1536V -
766.-
2523.-
10143.-
-ffirr
766 -
1071
4148.-
94B7.-
IS482 -
3118 -
9877 -
405.-
2181.-
I55BI.-
2415.-
7369 "
5935.-
15708 -
3506 -
10165 -
2181.-
15852 -
1071.-
5131 -
iSPfc
766 -
5103 -
Si
5647 -
9877 -
455 -
15979 -'
608S -
10165 -
16150.-
766.-
748 -
2462 -
3797 -
Sr
7359 -
6ZSS -
3592.-
17206 -
1979 -
11446.-
2966.-
17391.-
42(1 -
13840.-
IBI02 -
II42B -
2512 -
_.3»IP.--
17850.-
1495 -
9751 -
18370 -
280? -
18554 -
14879 -
S^
5298 -
6653 -
m^-
1 IOS2 -
1481,-
19550 -
6758 -
1071(1—
I7MI.-
Dl SWSAL
COST
2439 -
3842 -
1*91 -
5665.-
13437 -
882 -
2988.-
1743 -
5779.-
T!S"SC"-~
3861.-
1745 -
5784. -
iSS^
812 -
5129 -
I7B2.-
J778 -
13572.-
BB2 -
2961 -
6193.-
12716.-
6004 .
I7W -
ISWiL
2246 -
4594 -
3643 -
2303 -
IZ786 -
2443 -
3844.-
s^-
812.-
2988 -
1st
B82 -
591 -
492? -
6558,-
12954 -
3749.-
6551.-
253 -
I2BS6 -
2487.-
4594 -
570V.-
12788 -
3863 -
6610.-
23Q3.r-
12786 -
591.-
579B -
iSfc-
882 -
5211 -
6613.-
12788 -
6048 -
6551 -
12)55*-
ei66 -
«6» -
12786 -
882 -
380 -
2964 -
10638 -
17707 '-
4594 -
5101.-
3083 -
12786.-
2N6.-
BII7 -
2413.-
I27B6.-
3414.-
9372 -
12786 -
1350 -
1677 -
32V9.-
13276 -
1275.-
58V6 -
.5665 -
T37M.-
2066 -
1 1329 -
(3395 -
9S82 -
s^-
5636 -
4668 -
iSS^
10767 -
ity^
6679.-
i^r
TOTAL COMMIT!
COST
t 17,15V.-
t 27.H22--
t 27,659 -
t 27,793 -
» 27,912 -
$ 28,031 -
t 18,126 -
1 28,150.-
t 28,399 -
1 28,936 -
$ 18,437 -
t 28,495.-
t 18,638 -
$ 28,675 -
1 28,791 -
$ 18,834.-

t 29,119 -
t 29,992.-
t 30,177-
» 30,118,-
* 31, (26 -
t 31. 166 -
t 31,949 -
t 31,042.-
t 32,330
t 35,552 -
t 35,771.-
-17

-------
ton, while in Simulation No.  62, Rank No.  10, the fee at Site 2 has been in-
creased to $1.80 per ton.   This causes approximately a $500 increase in
total community cost per week and reduces the tonnage of waste that would
appear  at Site 2 from about 19% of the total to about  3%.  This precludes an
economical landfilling operation at Site 2 and shows  Simulation No.  92 to
be an impractical combination of sites under these conditions.

The Transfer Station at Site No. 4 appears in a number of the simulations.
It had been previously determined that the solid waste received at Site No.
4  could be transferred to Site No. 5  at a lower cost than to any other site.
The percentages of total waste  received at Site No. 4, appear in parenthe-
sis in Table III-2 and have been included in the percentages for Site No. 5.
With one exception,  the transfer fee was added to the disposal fee and be-
came part of the disposal  cost.  The  exception was Simulation No.  48, Rank
18.  This simulation and the unattractive economics of transfer stations for
use in the Metropolitan area were discussed in the preceding Section Dl. e .
of this Part III.                                                       •   ~

The amount of use a site would attract is highly sensitive to the fee charged.
In Simulations 57 and 54,  Ranks 21 and 24, the same two sites are used.
Where the disposal fee is  the same as in Rank 21,  Site 2  receives 26.72%
of the tonnage and Site  5 receives  the remaining 73.26%.  Where there is
a differential in fee  and Site 2 is 55 cents  per ton more expensive,  the per-
centage of tons  received changes to 11.35% and 88.65%.  Under a differen-
tial of this nature Site 2 tonnage would  be  cut by more than  half.

A similar  comparison can be made in Simulations 52 and 62,  Ranks 5 and 10.
If a 55-cent change was made in the price  per ton at Site 2, the expected
tonnage would drop from 19- 15% to 3.29%.

Simulation No.  98 is reproduced in Table  III-4 for reference  and explana-
tion.  Other  simulations appear in Exhibits III-l,  2 and 3.

The computer printout  is in terms of vehicle types,  totals  for all vehicles
and all  sites, and vehicle  distribution by disposal site.  The print-out in terms
of vehicle  type will be useful in predicting the patterns to be expected and
provided for when actual sites are designed and developed.   The "Totals for
all Vehicles" are in terms of cubic yards  per site which, in conjunction with
the topography of the site, determine the amount of  land required;  tons per
site aid in landfill equipment selection; vehicles per site determine scale
and "working face" requirements; haul cost and disposal cost together give
total community cost; and percent cubic yards and percent tons were  used
to calculate future land requirements at each site.

The printout "Vehicle Distribution by Disposal Sites" which is Page 2,
Table III-4,  in effect draws the boundary line that appears in Figure No.
Ill- }.  This line divides the area into parts, each of which contain the disposal
site where the sum of haul cost and disposal cost will be the least.  In the case
of Site 8, which did not appear in  the simulations, the boundary line was drawn
as discussed in Section D3.ji. of this Part III.

                                   Ill-18

-------
  TABLE
  Page  I
mr - 4-
ECONOMIC  SIMULATION  NO. 98 (TYPICAL)
  SIMULATION NUMBER   98
 • SITE  1 DISPOSAL FEE 1.25/TON
	TRANSFER FFE Q.OO/TON
         MINIMUM FEE 1.00
  SITE  3  DISPOSAL FEE 1.25/TON
                  FEE
          MINIMUM FEE  1.00
  SITE  5 DISPOSAL FEE 1.25/TON
                  FEE ft.ftQ/Tnh)
         MINIMUM FtE 1.00
  SITE  7 DISPOSAL FEE 1.25/TON
         TBtNSFFR FFF O.On/TON
         MINIMUM FEE 1.00
1
SITE
1
2
4
5
6
7
i

1
3
4
5
7
i
SITE
1
2
3
4
	 5.
6
PACKER TRUCK
CU YDS
44H
0
0
0
54?
VAM

SO
0
131
0
574
i
169
TONS
0
1367
0
1650
0


27
0
81
0
306
80
VEHICLES
69
0
232
0
388
0
92

HAUL COST
4.35
0.00
4.33
0.00
5.46
0.00
5.62

DISPOSAL COST
6.35
0.00
7.37
0.00
5.32
0.00
5.34


16
0
54
0
194
0
35
2.96 2.08
0.00 0.00
2.53
0.00
3.37
3.78
1.92
0.00
1.98
JL.OO
2.90
HEAVY TRAILER
CU YDS
43
0
25
0
0
__ 1U__
TONS
a
0
7
0
80
0
55
VEHICLES
2
0
7
0
29
0
10
7 PICK UP TRUCK
1
	 2-
3
4
5
7
1
SITE
2
4
6
	 7_
	 CU-YQS
63
0
238
0
999
0
173
TONS
50
0
190
0
719
0
127
TRANSFER VEHICLE
CU YDS TONS
22 4
0 0
a o
0
0
0
0

TOTALS FOR ALL
SITE
	 L.
2
	 3
4
t;
6
CU YDS
0
. 	 __2956-
0
7110
0
	 .2439..
13320
0
0
0
0

VEHICLES
TONS
.7j02-
0
. . 2380..
0
q?*7
0
10188
VEHICLES
52
227
918
0
142
VEHICLES
1
0
Q
0
0
0
0


VEHICLES
.240.
0
9.21
0
27b2
0
-- -527
4440
HAUL COST
6.25
0.00
4.20
0.00
0.00
6.15

HAUL COST
2.35
0.00
2.13
0,00
3.07
0.00
3.19
HAUL COST
9. HO
0.00
Bj-Q.fi.
0.00
0.00
0.00
0.00


HAUL COST
765,59
0.00
25£3-t2J
0.00
10143.46
0.00
2180.66
15612.94
DISPOSAL COST
4.84
0.00
1.37
0.00
3.47
0.00
6.92

DISPOSAL COST
1.28
0,00
1.13
0.00
1.03
0,00
1.12
DISPOSAL COST
5.00
0.00
0.00
0.00
0.00
0.00


DISPOSAL COST PCT Y
881,67 . 6,12
0.00 0.00
,2987,75 22.19
0.00 0.00
6613.37 53.38
0.00 0.00
2302,69 	 18.31
12785.69
! DUMP
SITE
1
2
3
4
5
6
7
4 LI6HT
TRUCK
CU YDS
51
0
254
0
1306
0
1122
TRAILER
SITE CU YDS
1 0
2 0
3
4
5
6
7
6 FLAT
SITE
2
3
4
5
6
7
1 AUTO
SITE
1
2
3
4
5
6
7
10 OTHER
SITE
1
2
3
4
5
6
7


PCT T
6.89
0.00
23.36
0.00.
51.70
0.00
l'8.06
9
0
62
0
3

TONS
59
0
331
0
1529
0
981


VEHICLES
20
0
90
0
409
0
153

TONS VEHICLES
* 4
0 0
6
0
54
0
2
16
0
BT
0
4
BED OR STAKE
CU YDS
125
0
480
0
1290
0
312
OR STATION
CU YDS
3
0
17
0
51
0
1"
VEHICLES
CU YOS
10
0
0
0
2
0
0






TONS
121
0
384
0
882
0
200
UGN
TONS
2
0
13
0
36
0

TONS
80
0
0
11
6
0





VEHICLES
31
0
128
0
273
- ~
-------
TABLE IIT - 4 ECONOMIC SIMULATION NO. 98 (TYPICAL)
Page 2

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103
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77
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A
0
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4

43
923
250
423
4
5
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	 _45____
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599
15
FEES

217
130
3
42
17

7
18
3
•
B
33
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7
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736
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2
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648
169
332
3
3
6
	 i»__ .
9
107
295
9

9.84
11.93 	
10. 84
5.75
9.68
4.60
3.60
6.05
4.09
4.40
3.75
11.09
5.17
13.22
4.68
9.73
4.26
3.17
4.17
1.50
3.62
5.16
4.87
1.59
2.53
14.80
14.68

11.39
9.27
6.24
9.69
17.31
8.50
7.76
3.64
4.09
7.82
6.67
5.73
8.99
3.63
3.10
3.53
6.14
2.97
3.16
3.50
3.02
1.78
3.37
4.08
2.82
2.70
5.53
7,59
4.27
4.32
9.66
5.45
9.65
5.76
5.81
6.95
4.90
7.62
6.77
3.60
3.30
3.86
.05 SITE 7
.69
.71
.22
.08
.70
3.55
2.30
1 .86
2.05
.89
.71
2.22
1.70
1.57

12.30
11.06
10.59
B.88
10.93
7.97
11.22
9.U-
13.62
12.27
11 .63
"•« III- 20
2_


1











5


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3
4
5

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18
19
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16
1 6
4
149
2

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9_

15

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1
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318
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20
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0
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8
6.6
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1
34
22
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40
659
t7
181
59
4
95
5
_24_
B
-------
         3.      Domestic Solid Waste Collection and Disposal in Eastern
 Pottawattamie County.

                ji.    General.  The rural communities of Pottawattamie
 County, like most rural communities throughout the country,  are not served
 by an organized solid waste collection system,  and generally the waste is not
 disposed of in a sanitary manner.

 Rural communities present special problems in solid waste handling because
 of their relative remoteness from each other and from Metropolitan solid
 waste handling  systems,  but with adequate cooperation between communities
 and with the proper organization it is feasible and economical for many rural
 areas to have organized solid waste handling systems.  Eastern Pottawattamie
 County  is one of these rural areas where an organized system is feasible and
 economical and the establishment of a solid waste handling system is recom-
 mended.

                _b.    Collection Systems. The contract for this study and
 report  specifically excludes the analyses of and recommendations for solid
waste collection systems.  But, because the disposal recommendations
 includes a single  sanitary landfill site to serve  all of this  rural  area in lieu
 of a  small facility serving each community,  we have included a  preliminary
analysis of a collection system for this area. It is important to note that the
analysis which is discussed in the  following paragraphs is only preliminary
and that detailed work is  necessary before the initiation of a collection
 system .

                      (1)    Existing Collection Methods. Present collection
and/or  disposal of solid waste in rural Pottawattamie County is typical of
rural communities. Part of the owners or occupants of dwellings and commercial
establishments have private service on a  regular  schedule from private haulers
and part haul their own waste to the local dump  on a regular schedule.  There
is also  a substantial part which burn the combustible waste and haul the resi-
due and incombustibles to the dump on an infrequent basis.

                      (2)     Recommended Collection System.  It is recom-
mended that the rural communities  in Eastern Pottawattamie County organize
a joint solid waste collection system to serve all of the communities in the
area.  This joint system could be organized under provisions of the "Joint
Exercise of Governmental Powers" found in Chapter E8E of the Code of Iowa;
or could be provided by the Public  Agency recommended in Part IV of this
report.

                — •    Scope of Collection Service

                      (1)    General. The scope of collection service concerns:

                           The customers to be served
                           The nature of materials to be  collected

                                   111-23

-------
                           The frequency of collection;
                           The point of collection,

                      (2)   Customers to be Served. It is recommended
that service be provided to all single family and small multiple family
dwellings in McClelland,  Iowa, and the  10 additional municipalities lying
east of a line through McClelland.

Commercial and industrial waste generally require  special collection
service.   This waste varies considerably in quantity and characteristics.
Private haulers have satisfactorily provided this service in the past and are
equipped to do so in the future.  However,  in the future, when a system has
been established and has  acquired  the necessary  operating skills and manage-
ment techniques, the municipalities may wish to  consider this service.  For
the immediate future, it is recommended that private contractors continue
to provide commercial and industrial service.

                      (3)   Material to be Collected. It is recommended
that all domestic solid waste which can be placed in approved containers
be collected regardless of quantity.

                      (4)   Frequency of Collection Service. It is recom-
mended that the frequency of the collection service be at least one collec-
tion each week on a five  day week schedule.  This system will provide the
communities with regular collections with approximately 
-------
                      (2)   Service Area. It has been assumed for purposes
 of this study that the service area is that portion of Pottawattamie County
 east of a line through McClelland, Iowa.  That portion of the county contains
 J.1 municipalities to be served by a Collection system.  The populations of
 these municipalities as determined by statistics of the U. S. Census Bureau
 and the Omaha-Council Bluffs Metropolitan area Planning Agency are shown
 hi the following list.  The numbers of dwelling units were determined by
 using the statistical figure of 3. 3 people per dwelling unit.

 Town                      1970 Population           Dwelling

 Avoca                            1,513                  459
 Carson                             569                  173
 Hancock                            250                   76
 Macedonia                          273                   83
 McClelland                         143                   44
 Mindon                             381                  116
 Neola                              884                  268
 Oakland                          1,351                  410
 Treynor                            274                   83
 Underwood                         399                  121
 Walnut                             725                  220
   Totals                          6,762                2,053

                      (3)    Waste Quantity for Collection.  It is assumed
 that domestic solid waste generation on a per capita basis is equal to that
 quantity measured in the  Metropolitan Area.   As shown in Table 11-24, the
 domestic  waste generation  per capita in 1970 is:

                      207,000 Tons  j- 515,800 People = 0.4 Ton/Person/Year.

 The  statistical dwelling unit contains 3. 3 people,  therefore the average
 weekly generation of domestic waste  is 51 pounds per dwelling  unit per week.

                      (4)    Disposal Site Location.  Ideally a solid waste
 disposal site would be located-at the centroid of all solid waste generated
 and disposed of in a particular area.  Sometimes this  location is impractical
Or inconvenient.   The centroid of solid waste  (and population) for eastern
 Pottawattamie County is 4 miles west of Hancock, Iowa.  It would be  more
 convenient to locate the disposal site nearer  to Hancock and nearer to U. S.
Highway No.  59 which is  the major north-south highway in that part of the
 county. It is recommended elsewhere in this report that a sanitary landfill
 facility be established in  the vicinity of Hancock, Iowa.

                      (5)    Road System.  The preliminary layout of the
collection route was made using a  1968  general highway and transportation
                                    ffl-25

-------
map of Pottawattamie County prepared by the Iowa State Highway Commission.
Only paved roads were  considered for the collection route.

                     (6)   Collection  Manpower and Equipment.  The major
portion of the cost of a  collection system is represented by the wages of its
Inbor force.  Consequently this is the area where careful planning can realize
the greatest cost savings.  This planning should minimize cost by laying out
the optimum  collection  route to be worked by the optimum size crew with
equipment that is compatible with the type and quantity of work to be accom-
plished.

Detailed collection system studies have shown that 2-man and 3-man collec-
tion crews bbth have their applications  depending upon the type of route being
served.  In the case of  eastern Pottawattamie County a 2-man crew was
selected.

The collection vehicle used in the preliminary route layout is a packer-type
truck with a 22 cubic yard capacity.  A more detailed study and future exper-
ience may show that a 20 C. Y.  truck would be adequate or that a 24 C. Y.
truck is required.  The difference in cost when amortized over 5 years if not
great.   It is important that the vehicle  have adequate capacity in  order to
avoid making extra trips.  At an average in-truck density of 581  pounds  per
C. Y. ,  a 22 C. Y.  packer truck could haul the solid waste from 250  dwelling
units in each load.

Previous studies  have shown that a 2-man crew  will collect on the average
1. 5 dwelling units per minute including driving time between dwellings.

Highway driving time has been computed on the basis of 50 m. p. h.  which  is
equivalent to 1. 2 minutes per mile, (1. 2 M/mi).

It is assumed that the crew will work a 5-day week and devote 8 hours or
480 minutes per day (including 30-minutes break time) on the collection
route.

Table III-5 shows the preliminary daily work schedule for the collection
route.   It is assumed that the sanitary  landfill disposal facility is near
Hancock, Iowa, and that the  collection  crew will work out of Hancock.
                                IH-26

-------
   TABLE III-5.
EASTERN POTTAWATTAM1E COUNTY
DOMESTIC REFUSE COLLECTION ROUTE
AND PRELIMINARY DAILY WORK SCHEDULE
MONDAY
                                MINUTES
1.
2.
3.
4.
5.
6.
7.
8.
9.
10.
11.
12.
13.
14.
Hancock to Treynor
Treynor 83 DU
Treynor to Carson
Carson 173 DU
Carson to S. L. F.
Unload
S.L.F. to Macedonia
Macedonia 83 DU
Macedonia to Oakland
Oakland 167 DU
Oakland to S. L.F.
Unload
Breaks
Totals 506 D. U.
23 mi.@ 1.2 M/rni
@ 1.5 DU/M
10.2 mi@ 1.2 M/mi
@ 1.5 DU/M
12.8 mi@ 1.2 M/mi

15.8 mi@ 1.2 M/mi
@ 1.5 DU/M
9.4 mi @ 1.2 M/mi
@ 1.5 DU/M
6.4 mi @ 1.2 M/mi


77.6 mi
28
56
13
116
16
5
19
56
12
112
8
5
30
476
TUESDAY
1.
2.
3.
4.
5
6.
7.
8.
9.
10.
S. L.F. to Oakland
Oakland 243 DU
Oakland to S. L.F.
Unload
S.L.F. to Walnut
Walnut 220 DU
Walnut to S. L.F.
Unload
Breaks
Totals 463 D. U.
6.4 mi @ 1.2 M/mi
@ 1.5 DU/M
6.4 mi @ 1.2 M/rni

13.4 mi @ 1.2 M/mi
@ 1.5 DU/M
13.4 mi @ 1.2 M/mi


39. 6 mi
8
162
8
5
17
147
17
5
30
400
WEDNESDAY
1.
2.
3.
4.
5.
6.
7.
8.
9-
10.
11.
12.
13.
14.

S.L.F. to Avoca
Avoca 250 DU
Avoca to S. L. F.
Unload
S. L. F. to Avoca
Avoca 209 DU
Avoca to S. L. F.
Unload
Breaks
S.L.F. to Hancock
Hancock 76 DU
Hancock to S. L. F.
Unload
Totals 535 D. U.

7.2 mi @ 1.2 M/mi
1.5 DU/M
7.2 mi @ 1.2 M/mi

7.2 mi @ 1.2 M/mi
@ 1.5 DU/M
7.2 mi @ 1.2 M/mi



@1.5 DU/M


30.8 mi
III- 2 7
9
167
9
5
9
140
9
5
30
4
51
4
5
447


-------
   Table III-5 (cont'd)
THURSDAY

1.    S. L. F. to Nooia
2.    Neola Z50 DU
3.    Neola to S. L. F.

-------
                .£•    Collection System Cost Estimate

                      (1)    General.   The cost estimate for the collection
 system based on current prices and wages, appears in Table I1I-6.  The
 following paragraphs discuss each major item considered.
   4
                      (2)    Basic  Cost Data.  The basic cost data are the
 items used to develop total annual  cost of operation.  They include:  the
 initial purchase of the collection vehicle; the cost of a small building to be
 built at the landfill site to provide  facilities for the operating personnel;
 the cost of maintaining,  operating, and amortizing the operating equipment
 plus a rental fee for a spare truck if required; and miscellaneous costs,
 overhead,  and contingencies.

                      (3)   Annual Costs.   The annual costs include the
 expense of repaying the  initial debt and the recurring annual expense of
 operating personnel and equipment.

 The debt expense  provides for a 6% -  5 year amortization to purchase the
 original packer truck, and a 6% - 20 year amortization to pay for the
 personnel  facilities and  garage.

 Annual  operating expenses include salaries, equipment costs, miscellaneous
 costs and contingencies.

 The sum of debt expense plus operating expense gives the total annual cost
 of $31, 700. This  figure is used to compute the annual fee to be  charged
 each dwelling unit.

                      (4)   Collection Fee Computation. The collection fee
 or cost per dwelling unit is the sum of collection cost plus debt  service reserve
 plus  disposal cost.

 The collection fee was developed from the  estimate of annual cost for providing
 collection  service to 2053 customers.

 The cost of debt service reserve is not an  actual cost but is  a revenue  that
 must be provided  and set aside for protection  of the bond buyers if the  capital
 funds are raised through the sale of bonds.  It is  taken as 40% of the annual
debt expense of $3300.

 The disposal cost is based upon an annual domestic waste quantity of 1. 32
tons per dwelling unit  and a disposal fee of $1.40 per ton as  recommended in
 Part 1II-E-7 of this report.
                                   111-29

-------
     TABLE III-6.  COST ESTIMATE. DOMESTIC WASTE COLLECTION
                   EASTERN POTTAWATTAMIE COUNTY

 A.       BASIC COST DATA
         1.     Initial Purchase of Equipment
                (one time purchase only)
                1 packer truck @$11, 000                $11,000
         2.     Personnel Facilities & Garage
                800 s. f. @  10. 00/s. f.                     8, 000
         3.     Operating Personnel
                Salaries                      $17,150
                Fringe Benefits and Salary
                 Expense f 17%                2.950    20, 100
         4.     Operating Equipment, Maintenance,  Operation and
                 Amortization
                1 truck @ $3,900
                1 rental @___5_P_0_                         4,400
         5.     Misc. Expense, Overhead & Contingency   3,900

 B.       ANNUAL COSTS

         1.     Debt Expense

                a.     Initial Purchase of     $11,000
                      Equipment
                      5 yrs. @ 6% = 0. 23740
                      . 2374 x 11,000 =                  $2,600
                b.     Personnel Facilities and $ 8, 000
                      Garage
                      20 yrs. @ 6% = . 08718
                      . 08718 x 8,000                        700
                c.     Total Debt Expense                         $  3, 300
         2.      Operating Expense
                a.    Operating Personnel                20, 100
                b.    Operating Equipment                4,400
                c.    Misc. & Contingency                 3,9QQ
                d.    Total Operating Expense                      28.400
         3.      Total Annual Cost                                $ 31,700

C.       COLLECTION FEE COMPUTATION

         1.      Annual Cost       $31,700
         2       Subscribers           2, 053 Dwelling Units
         3.      Cost Per Dwelling Unit
                a.    Collection
                     31,700s- 2053 DU =                $15.48
                b.    Debt Service Reserve
                     40% (3300. )  --- $1, 320
                     1,320 .--2,053 DU =                    0. 64
                c.    Disposal
                     1. 3£ tons per Dwelling Unit @ $1.40   1. 85
                d.    Annual Cost Per Dwelling Unit      $ 17. 97
                                 III-30

-------
                 {.    Summary. The economics  of an organized rural
 rommunily effort for the collection and disposal of domestic solid waste
 compare favorably with those of large metropolitan systems.

 The annual fee of approximately $18. 00 per year  per dwelling unit for the
 communities in eastern Pottawattamie County provides for once-a-week
 collection and disposal of all domestic solid waste of residential subscribers.
 Presently, subscribers to the City operated collection system in Council
 Bluffs pay $15. 00 annually for a service which collects kitchen waste only.
 The City of Omaha system,  operated under a  contract, provides for collec-
 tion and disposal of all domestic and some commercial waste.   The cost  of
 the domestic portion is approximately $12. 00 per dwelling unit.  A recent
 study in Des Moines,  Iowa,  recommended an  annual fee of $10.80 per
 dwelling unit for once-a-week collection and disposal of domestic waste.

 The present costs to the  residents in the communities  in eastern Pottawattamie
 County for hauling and disposing of domestic solid waste are not known, although
 private service rates of $24. 00  to $36. 00 per year are common. It is reason-
 able to assume that one system  serving the aggregate community is considerably
 less expensive than that of each  household hauling and  disposing of its solid
 waste  or contracting privately for that service. In addition, the nuisance of
 several open burning dumps would be eliminated by the sanitary landfilling
 of the waste at one disposal site.

 Open burning dumps have been declared unlawful after  April 1,  1970, in the
 State of Iowa by its Government. An organized system for the  sanitary collec-
 tion and disposal of solid waste  in eastern Pottawattamie County is suggested
 to be a feasible and economical  answer to this recent legislation.

         4.     Sanitary Landfill Cost Estimates

                a..    General. The cost estimates for  five combinations of
 landfill sites are summarized in Table III-7.  The itemized cost estimate for
 the combined operation of Sites  1, 3, 5,  7 and 8 is presented in Table III-8.
 In the following paragraphs each major cost item  is considered and discussed.
 Detailed estimates for other combinations of landfill sites are found in the
Appendix,  Exhibits III- 4 through 7.  The estimates are based upon current
prices and wages.  It will be necessary to adjust these costs prior to implem-
entation of the landfill operations,  when the final designs are made and final
conditions are known.

The estimate in Table III-8 for the 5-site operation is based upon operating
the 2 smaller sites, Sites 1 and  8 for eight hours  per day, 5 days per week,
and sites  3,  5 and 7 for 12 hours per day, 6 days  per week.  It is probable
that sites 3,  5 and 7 would be open to the public eleven hours per day with
                                   111-31

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one hour per day allotted at the end of the day to permit all refuse to be
covered and incidental clean-up to be accomplished.  Additional details of
individual site operations are found in Paragraph _j_, and Table III-9.

                _b.    Basic Cost Data  (Refer to Table III-8)

                     (1)   Land Costs. Land costs were developed from        H
the estimated land  requirements as seen in the table and further discussed
in Part II1-E of this report.  An informal investigation of land prices for the
selected general areas  provided the estimated land cost per acre.

                     (2)   Initial Site Development.   These costs were
developed by analyzing  the required physical developments necessary for
placing the landfill sites in readiness for operation.

                     (3)   Annual Site Maintenance and Development.  These
costs are for  the expected general maintenance and annual expansion required
for site upkeep and continued operation.

                     (4)   Equipment Purchase.   This  estimated cost is for
the equipment recommended for operation  of the 5  sites.  The distribution  of
the equipment is itemized in Table III-9.  This cost is a one-time expenditure
for the initial procurement of the equipment.  Funds for replacement of
equipment are provided for in the operating costs as discussed in the following
paragraph.  There are  many types of heavy equipment suitable for sanitary
landfilling operations.  The preliminary equipment selection made for estim-
ating purposes in this report is based upon anticipated conditions at the
landfill sites.   Final equipment selection can be made only after the actual
sites are designed and more extensive soil analyses have been made.  The
equipment selections should minimize total equipment costs which include
initial cost, maintenance and operating costs, and  replacement costs.


                     (5)   Equipment Maintenance,  Operation and Amortization.
These  estimated costs are for the maintenance, operation (excluding labor) and
amortization of the required equipment for the 5 sites.  The costs are based
upon operating the primary equipment 8 or 12 hours per day, 5 or 6 days per
week.

Support equipment  such as the grader, tractor-mower,  and water trucks
would be shared by the  4  sites in the Metropolitan area and rented at Site 8  in
eastern Pottawattamie County.  Equipment operation hours are itemized in
Table III-9.  Included in the equipment hourly rate  is the estimated amortiza-
tion of each piece of equipment.   This amortization will prepay the  cost of
replacement by establishing an equipment escrow fund to be used with trade-in
equipment for necessary  replacements.  The spare equipment wouId be avail-
able to any of the sites  when needed.
                                  IH-3 2

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                      (6)    Labor.   These are the estimated costs for the
personnel required to operate the required equipment and facilities of the 5
sites, exclusive of the management categories in the Agency operation.   Wage
rates include fringe benefits.  For additional details  of labor distribution see
Table III-9 and the discussion thereof.

 *                    (7)    Agency Headquarters and Maintenance Building.
This  estimated cost is to provide for the facilities and equipment necessary
to the Agency operation.  This facility would be located at one  of the landfill
sites  and would be in addition to' the personnel facility provided for the labor
force at that site.   Extensive maintenance of landfill equipment would be
handled at the Headquarters Maintenance facility while day to day preventive
maintenance would be accomplished at the individual  sites.

                      (8)   Agency Operation. This is the estimated cost
for the wages of management personnel and for the  operating overhead of the
Agency.

                      (9)   Miscellaneous Expense and Contingencies.  This
is the estimated cost of the miscellaneous expenses and contingencies which
normally could be expected during the course of Agency operations.

               £.     Annual Costs.  The following annual cost  computations
are based upon the itemized requirements presented in  Table III-8,  in which
some  expenditures are one-time  initial expenses  and the remaining are annual
reoccurring expenses.  The one-time expenses are assumed to be financed
through the sale of revenue bonds, repayable at 6%  interest over a  20-year
period.

                             ANNUAL COST DATA
                One-Time Expenses (20 yrs. @ 6% = 0. 08718)
                Land Cost                        $  996, 000
                Initial Site Development              482,000
                Equipment Purchase                 509, 000
                Hdqtrs.  Bldg.                        130, OOP
                                         08718 x $2 ,117, 000=      $184,600

                Reoccurring Annual Expense

                Site Maint.  & Development        $   81,500
                Equip. M. O.  & A.                   241,500
                Labor                               238,100
                Agency Operation                     67,600
                Misc.  & Contingencies            	62, OOP
                                                                   $690,700

                Total Annual Cost                                   $875, 300

                                      III-3 3

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                cl.    Fixed and Variable Annual Costs.   Following is a
summary of fixed and variable annual costs for the 5 sites.  It is assumed
that the fixed costs will be necessary expenditures which will occur each year
and will not change as the quantities of waste change throughout the years,
while the variable costs will be dependent upon the quantity of solid waste
received each year. The following costs are used in the development of Unit
and Total Operation Costs:

                                      Fixed Costs   Variable Costs

        One-Time Expense               $184,600
        Annual Development                             $  81,500
        Equip.  MO&A                      17,000*       224,500
        Labor                            139,600          98,500
        Agency Operation                  67, 600
        Misc. &  Contingencies           	          62, OOP
                                        $408,800   +    $466,500=   $875,300

          # Pickup Trucks & Miscellaneous Equipment

               £.    Quantities for Unit and Total Costs.  The following quan-
tities were established from the information given in Table 11-26.

                                             Ac. Ft.       Tons
          1st Year         1970              628           751,200
          4th Year         1973              580           691,000
          Average Year    1982              744           884,300
          Final Year       1995              978          1,158,400

These quantities are used to establish unit and Total Operation Costs for the
5 sites.

               _f.     Unit and Total Costs of Operation.  The following compu-
tations establish Unit and Total Costs of operation for the 5 sites.

Part of the cost of operation of the disposal facilities are fixed costs which do
not vary with the amount of solid waste  disposed of.   The remainder of the costs
are directly proportional to the amount  of solid waste  and because of this, the
unit cost of operation will vary each year.

          (1)    1st Year 1970  - 628 Ac-Ft. or 751,200 Tons
                Fixed Costs $408,800 -c- 628 Ac-Ft. =      $650/Ac-Ft.
                Var.  Costs $466.500 -:- 628 Ac-Ft.  -      $740/Ac-Ft.
                Total       $875,300                    $1, 390/Ac-Ft.

                $875, 300 -:- 751, 200 Tons -- $1. 16/Ton
          (2)    4th Year 1973  580 Ac-Ft. or 691, 000  Tons
                Fixed Cost                                $408,800
                Variable Cost 580 Ac. Ft. x $740/Ac-Ft.     429,200
                                                          $838,000
                                    in-34

-------
                838,000-:- 691, 000 Tons = $1. 21/Ton
                838,000-:- 580 Ac-Ft.    = $1, 445/Ac-Ft.

          {3)   Average Yr.  1982 - 744 Ac-Ft. or 884, 300 Tons
                Fixed Cost                                $408,800
                Variable Cost 744 Ac-Ft.  x $740/Ac. Ft.      550,600
                                                          $959,400
                $959,400 -:- 884, 300 Tons = $1. 09/Ton
                $959,400 -:- 744 Ac-Ft.  = $1, 290/Ac-Ft.
          (4)   Final Year 1995  - 978 Ac-Ft. or 1, 158,400  Tons
                Fixed Cost                               $408,800
                Variable Cost 978 Ac-Ft.  x $740/Ac-Ft.    $723,700
                                                        $1,132,500

                $1, 132, 500 -:- 1, 158,400 Tons = $0. 98/Ton
                $1,132,500-:-   978 Ac-Ft.  ^  1,160/Ac-Ft.

                _g.    Bond Debt Service Reserve.  Bond buyers insist that the
 revenue be higher than the theoretical  amount required to meet debt service
 payments.   This extra revenue is known as debt service  reserve or premium.
 In this estimate it is based upon 40% of the debt service and is equal to 0. 4
 ($184,600) or $73,800 per annum.  It is not actually a cost but must be included
 in revenue computations.  The debt service reserve will be a fixed amount, but
 the unit cost of this reserve varies with the total tonnage as follows:

                Istyr.  1970  $73, 800 -:- 751, 200 Tons = $0. 10/Ton
                4th yr.  1973  $73, 800 -:- 691, 000 Tons = $0. ll/ Ton
                Avg. yr. 1982   $73, 800-:- 884, 300 Tons   $0. 09/Ton
                Final yr. 1995 $73,800 -:- 1, 158, 400 Tons  - $0. 07/Ton

                h.    Summary of Unit Costs

                              Operation Cost     Debt  Service     Total
                     Year        $/Ton	    Reserve Cost      Unit Cost
                                                   $/Ton          $/Ton

                     1970        $1. 16             $0. 10           $1.26
                     1973        $1. 21             $0. 11           $1. 32
                     1982        $1. 10             $0. 09           $1. 19
                     1995        $0.99             $0.07           $1.06

               _i.     Individual Site Data. The data in Table III-9  is a breakdown
of the basic site data which supports the  cost estimate in Table II-8 for Sites 1,
 3, 5,  7 and 8.

                     (1)    Refuse Accumulation and Land Requirements.  The
accumulation of solid waste from 1970  through 1995 determined by  the summation
                                     III-35

-------
of annual projections was divided by the anticipated average depth of landfilJed
refuse to determine the necessary land area required to contain that refuse.
That acreage was multiplied by 1. 2 to provide 20% additional area for roads,
setbacks, site  screening berms and other non-fillable  areas.   It was assumed
that land would be purchased in multiples  of 40 acres.

                      (2)   The  daily quantities of refuse were obtained by       »
dividing annual projections  by the number of days  per year each site is expected
to be open to the public.   Sites 1 and 8 were assumed to be open and operating
5 days per week or 260 days per year while the remaining 3 sites would be open
and operating 6 days per week or 312 days per year.  These daily quantities
are indicative of the level of activity at the individual sanitary  landfill facilities
and were used  to make the tentative selection of the landfill equipment and the
labor force requirements.

                      (3)   The  initial site development and cost thereof is
itemized for each individual site in this  section of the table.

                      (4)   The  cost and distribution of the landfill  equipment
is itemized in this part of the table.  Each site has what might be termed  primary
equipment to be used exclusively at an individual site.   In addition the sites will
share other equipment such as the grader, mower, trucks, and spare equipment.

                      (5)   The  solid waste that each site would receive will
require a certain number of hours of landfill equipment operation.   The estimate
of the required hours  of operation appears in this  part of the table.   These hours
will vary depending upon the level of activity at each site, the length of the
working day, and the number of days per week the site  is in operation.

The hours of operation for equipment which is shared by the landfill sites is
prorated to those sites on the basis of tons per day of refuse received and/or
land area.

It is assumed that a. grader and mower will be rented when required at Site 8
in eastern Pottawattamie County.

Spare equipment will generally replace equipment that is "down" for repairs
or maintenance but it  may be used during  peak hour of operation, if necessary.
For the latter reason, a few hours of operation have been assigned  to the  spare
equipment to provide for this possibility and for other  contingencies.

                      (6)   Equipment operator hours are determined by
summing equipment operations hours exclusive of the hours shown for spare
equipment and  exclusive of the hours shown for the scrapers which  are not
self-propelled.
                                    Ill-36

-------
At Site 8 it has been assumed that the loader will operate 6 hours per day - 5 days
a woek or 1560 hours per year,  but the operator will work 8 hours per day - 5
days n week or 2080 hours per year.  Rental equipment is assumed to require
300 additional operator hours per year.  Therefore,  the total operator hour
requirement is 2080 hours f 300 hours  - 2380 hours.

«                     (7)    Labor hours per site are itemized in this portion
of I hi* table.  In addition to the equipment operator hours discussed in the
previous paragraph, the hours for laborers, foremen and gatekeepers are
shown.  It is assumed that laborers will work forty-hour week.   Sites 1 and 8
because of their relative low level of activity have no laborers.   Sites 3 and 7
have 2 laborers each, and Site 5 has 4 laborers.  Neither Sites  1 and 8 have
foremen as such.  Sites 3, 5 and 7 are  assigned foremen hours  at the rate of
8 hours per day,  6 days per week.  Gatekeeper hours are based upon 8 or 12
hours per day and 5  or 6 days per week, depending on the site.

Site 8 in eastern Pottawattamie  County  is essentially a one-man operation
with the equipment operator handling equipment operation in addition to acting
as gatekeeper and taking care of any incidental chores.
                                    Ill-37

-------An error occurred while trying to OCR this image.

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TABLEIII-8  BASIC COST DATA  FOR SITES 1, 3. 5. 7 and 8
1 . Land Cost
Site Acres Cost/Ac.
No. 1 South West 80 $1200
No. 3 North West 200 1200
No. 5 South East 480 1000
No. 7 North East 160 1000
No. 8 E. Pott. Co. 40 500
Total 960
2. Initial Site Development
Site 1 South West
Site 3 North West
Site 5 South East
Site 7 North East
Site 8 E. Pott. Co.
Total Initial Development Cost
3. Annual Maintenance and Site Development
Site 1 South West
Site 3 North West
Site 5 South East
Site 7 North East
Site 8 E. Pott. Co.
Total Annual Maintenance and Development
4. Equipment Purchase

Cost
$ 96,000
240,000
480, 000
160,000
20,000
$996,000

66, 500
112,000
162,500
112,000
29,000
$482,000

10,000
20, 000
30,000
20,000
1,500
$ 81, 500
$509,000
                           III-3 9

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Table III-8 Continued

5.  Equipment Maintenance, Operation and Amortization

    Item                           Hrs. /Yr.          Rate/Hr.       Cost/Yr.

    Track Loader, 170 FWHP      2,080             $10.00         $20,800
    Track Loader, 275 FWHP      2,496              15.00           37,400
    Track Loader, 115 FWHP      1,560               7.00           10,900
    Dozers,  125 FWHP             7,488               9.00           67,400
    Scrapers                      (2,496)*             3.00            7,500
    Compactor, 400 FWHP         2,496              19.00           47,400
    Grader,  125 FWHP             2,496               5.50           14,800
    Water Trucks                  2,496               4.00           10,000
    Tractor Mower                 1,248               2.00            2,500
    Trailer                       (  100)              3.00              300
    Dump Truck                  (  200)              5.00            1,000
    Pickup Trucks                                                     5,000
    Misc.  Rental                                                      12,000
    Grader                          200               5.50             1,100
    Tractor Mower                   100               2. 00              200
    Dozer, Spare,  125 FWHP      (  200)              9.00             1,800
    Wheel Loader, Spare, 130FWHP(  2QQ)              7.00             1,400

                                  25,856                            $241,500
    Equipment Operators          23,180                4.25        $98,500
    Laborers                     16,640                3.25           54,100
    Foremen                      7,488                4.75           35,600
    Gatekeepers                  13,312                3.75           49, 900

    Total                                                           $238, 100

7.    Headquarters and Maintenance Building

    Office and Maintenance Building                                   $ 80, 000
    Office and Maintenance Equipment                                   50, OOP
                                                                    $130, 000

8.   Agency Operation

    Salaries                                                         $ 51, 000
    Overhead                                                          16, 600
                                                                     $ 67,600

9.   Miscellaneous Expense and Contingencies                         $  62, 000

*NOTK;  Equipment hours in parentheses are not included in equipment operator
hours for labor costs.
                                    Ill-40

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                      TABLE III - 9  BASIC SITE DATA FOR SITES 1, 3,  5,  7 and I
1.





2




3.













4














5
















Waste Accumulation and Land Requirement
a
b
c
d

Ton:
a
b
c

Accumulation in acre feet* (19,870)
Fill depth in feet
Fill area required in acres
Purchase - acres (960 total)
^Compacted and seasonally adjusted
s of Waste per Day
Operation, days per week
Tons per day 1970**
Tons per day 1995**
#*Seasonally adjusted
1800
30
60
72
80


5
220
480

4350
30
145
200


6
510
850

9770
24
407
48O


6
1210
1750

3290
24
137
165
160


6
410
580

Initial Site Development and Cost
a.
b
c
d
e.
£
g
h
I
]
k
1

Buildings, Scale House & Pers Fac
Scales
Scale Equipment
Watermam
Perim Fence
Entr Fence
Gravel Surfacing
Grading
Landscaping
Area Lighting
Apron Pavement
Miscellaneous
Totals
20,000
	
	
10,000
3,500
2,000
2,000
8, 000
6,000
2,000
10, 000
3, OOP
$66,500
30, 000
9,000
10, 000
10,000
6,500
I.. 000
4,000
15,000
8, 000
3,500
10,000
4,000
$112,000
30,000
18.000
10,000
15,000
10,000
2,000
10, 000
30,000
12,500
•5,000
10,000
10,000
$162,500
30,000
9,000
10,000
10,000
6,500
2,000
4,000
15,000
8, 000
3, 500
10,000
4,000
$112,000
Equipment Costs and Distribution
a
b
c
d
e
f
g
h
i
J
k
1
m

3 Track Loader
2 Dozers
2 Scrapers
1 Compactor
1 Grader
2 Water Trucks
1 Tractor Mower
5 Pickup Trucks
1 Lowboy Trailer
1 Dump T ruck
Miscellaneous
1 Doze r (Spare)
1 Wheel Loader (Spare)
Totals (Total equipment $509, 000)
46,000
	
	
	
2,500
	
200
4, 000
1,400
2,400
1,600
7, 000
8,400
$ 73,500
....
35,000
25,000
	
5, 000
4, 000
400
4,000
1,400
2,400
2,200
7,000
8,400
$ 94,800
70,000
	
	
74,000
12, 500
8,000
1, 000
4, 000
1,400
2,400
4, 000
7, 000
8,400
$192,700
....
35,000
25,000
	
5,000
4,000
400
4,000
1,400
2,400
2,200
7, 000
8.400
$94,800
Equipment - Hours per Year
a
b
c
d
e
f
g
h
i
J
k
1
m
n
0

Track Loader, 170 FWHP
Track Loader, 275 FWHP
Track Loader, 115 FWHP
Dozer
Scraper
Compactor
Grader
Water Truck
Tractor Mower
Grader (Rental)
Tractor Mower (Rental)
Trailer
Dump Truck
Dozer (Spare)
Wheel Loader (Spare)
Total
2,080
	
	
	
	
	
248
	
124
	
	
(20)
(40)
(40)
( 40)
2,592

	
	
3,744
(1,248)
	
500
624
250
	
	
(20)
(40)
(40)
(40)
6,506
....
2,496
	
	
	
2,496
1,248
1,248
624
	
	
(20)
(40)
(40)
( 40)
8,252
....
	
	
3.744
(1.248)
	
500
624
250
	
	
(20)
(40)
(40)
( 40)
6.506
                                                                                                    Site 8
                                                                                                      665
                                                                                                       24
                                                                                                       18
                                                                                                       33
                                                                                                       40
                                                                                                        5
                                                                                                      110
                                                                                                      130
                                                                                                    10,000
                                                                                                    5,000
                                                                                                    2,300
                                                                                                    1,600
                                                                                                      900
                                                                                                    3, 000
                                                                                                    2, 000
                                                                                                    1,000
                                                                                                    2,000
                                                                                                    1,200
                                                                                                  $29,000
                                                                                                   28,000
                                                                                                    4,000
                                                                                                    1,400
                                                                                                    2,400
                                                                                                    2, 000
                                                                                                    7, 000
                                                                                                    8,400
                                                                                                  $53,200
                                                                                                    1,560
     NOTE:   1   40Hr /Wk x 52 Wk/Yr = 2080 Hr /Yr
                  48 Hr /Wk x 52 Wk/Yr = 2496 Hr  /Yr
                  72 Hr /Wk x 52 Wk  /Yr = 3744 Hr  /Yr
              2   Equipment hours in parentheses are not included in equipment operator hours for labor costs
Annual Equipment Operator Hours
Labor Hours per Year
      Equip  Operators (Total 23, 180)
      Laborers (Total 16,640)
      Foremen (Total 7,488)
      Gatekeeper  (Total 13,312)
                                             2,452
                                             2,452
                                             2,080
                                                           5, 118
5,118
4, 160
2,496
3,744
8, 112
8,320
2,496
3,744
                                                                                     5, 118
5, 118
4, 160
2,496
3,744
                                                                                                    2,380
                                                                                                    2, 380
                                             m-4i

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         5.      Summary -  Resulting Site Combinations .   The 28 economic
     simulations  shown in Table III-3 were reduced to four for final considera-
tion.   All simulations containing Sites 2, 4,  or 6,  were deleted when Sites
2, 4 and 6 were eliminated for reasons discussed in Part III.D.6.

The  four remaining simulations provided four combinations of sites shown in
Table  III-10.  A  fifth combination  resulted by  adding Site 8 to the Sites 1,  3,
5, 7 combination.

Site  No. 8 did not appear in the economic simulations because it was imprac-
tical to include as part of this study the  detailed measurement of waste quan-
tities at the numerous small disposal facilities in eastern Pottawattamie
County.  The site combination containing Site  No.  8 could not be simulated
and the figures in Table III-10 for  that combination were arrived at by compu-
tation  and/or proportion.

The  five site combinations were further analyzed and compared by developing
the cost estimates summarized in Table III-7  and by developing the community
costs which appear in Table III-10 which are discussed in the following para-
graphs:

To develop the 1970 community costs for a particular site  combination,  the
calculated initial disposal fee and  the projected  1970 solid waste quantities
and population were used.

The  "Calculated  Initial Disposal Fee" was determined by cost estimate after
the economic simulations (or in the case of Site No. 8, the computations)  pro-
vided the  necessary information for determination of land,  equipment, and
labor requirements at the sites.

The  "1970 Haul Cost/Week" was determined by  multiplying the simulation haul
cost by the ratio of 1970 tons of waste to the simulation tons of waste.  In the
combination  containing Site  No. 8  the Haul  Cost/Week was  assumed to be in
direct proportion to population served.  The haul cost was determined by
multiplying the haul cost for the Sites 1, 3,  5, 7 combination  by the population
ratio of 535,940/515,800.  The assumption  made, implies that unit haul costs
in rural Pottawattamie County are  equal to unit  haul costs in  the Metropolitan
area.  The average haul distance in the  rural  area will be greater but the
round  trip time will be less because  of less  restrictive speed limits.

The  "1970 Disposal Cost/Week" was determined by multiplying the simulation
disposal cost by the ratio of 1970 tons to the simulation tons and then by the
ratio of initial fee to simulation fee.  The simulation fee  in these combina-
tions was uniformly $1.25 per ton.  The 1970  Disposal Cost/Week for the
Sites 1, 3, 5, 7, 8 combination was obtained by multiplying the 1970 tons per
week by the  disposal fee of  $1.40  per ton.

The  "1970 Community Cost/Week" is the sum of haul cost and disposal cost.

                                     Ill-42

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in-43

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The  "1970 Community Cost/Year" is  52 times the weekly cost.

It should be noted that the 1970 Community Cost/Year will be  less than present
day costs.  Haul costs will be reduced because of the reduced haul times and     «
distances provided by multiple disposal sites.

Disposal coats will be reduced because the fee of $1.40 per  ton recommended     *
in this report for the operation of Sites 1, 3,  5,  7 and 8 is 20£ less than the
present fee  at the Douglas County Sanitary Landfill.  The present contract
between the City of Omaha and the privately operated sanitary landfill east
of the Mormon Bridge provides for the disposal of 100, 000 tons of waste  per
year at a  cost of $180,000 or $1.80 per ton.

Of the five combinations of sites shown in Table III-10, four are developed
and analyzed for the intended use by the Metropolitan area and the adjacent
rural areas of the three counties.

Although the two-site combination of Sites 3 and  5 is the most economical,
this  combination does not provide the convenience to the community,  nor
would it serve the future expanded Metropolitan area nearly as well as the
Sites 1, 3, 5,  and 7 combination.

Either of  the combinations containing three  sites is an  improvement over
the two-site combination, but neither is the optimum combination required
to satisfy the  present and future needs of the community.  The addition of
a third facility at Site 7  is quite  economical and it would receive  the quanti-
ties  of solid waste now and in the future to make it self-sustaining but it
dues nothing for Sarpy County and southwestern Douglas County.   The addition
of a  third facility at Site 1 is  also reasonably economical and even though its
immediate use is somewhat marginal, its  projected use recommends its
establishment,  and its location satisfies both the present and  future require-
ments of western Sarpy  County and southwestern Douglas County.  Both Sites 1
and 7 have points in their favor, but neither when individually in  combination
with Sites 3 and 5 present a satisfactory solution to the 3-county  area solid
waste disposal problem.

The  combination of sites which does meet the present and future needs of the
Metropolitan area is the combination  of Sites 1, 3, 5 and 7.  The added con-
venience provided the community and the  locations which provide for the  ex-
pansion of  the  community far outweigh the  additional cost of  less than 1/2  of
1% required to add Sites 1 and 7 to the basic  2-site  combination of Sites 3 and  5.

To further illustrate the advantages of the multiple  site combination of 1, 3,
5 and 7 in the Metropolitan area, the  savings that the City of Omaha could
realize on its present 10-year solid waste collection contract were investigated.
It was found that during  the survey week of October 2-8,  1968, 1708.88 tons of waste
were collected and hauled away by the City's contractor at a cost of $20,  637.53
or an average cost of $12. 08  per ton.  If at that time, the City had had the option
of directing its  contract hauler to  any of the 4 sites instead  of only being  able
to utilize existing Site 2, the  average cost would have been $11. 69 per ton.   The
                                   in-44

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 savings for that week would have been $665. 65,  and over a year's time this
 amounts to approximately $34,000.  The savings result solely from the
 shorter haul distances provided by the multiple disposal site system.   The
 Cky of Omaha could realize the savings through the Overhaul provision in
 the collection contract.  The collection contract will be in effect through 1978
 and cost adjustments will be made each year dependent upon the Consumer
 Price Index of the previous year.

 The recommendation of Site 8 near Hancock, Iowa  is independent of,  and in
 addition to, any combination of sites considered for the Metropolitan area.
 Facilities for the 3-county area would be incomplete without a sanitary
 landfill in eastern Pottawattamie County.  Site 8 adds  28,200 tons of solid
 waste, and 20, 140 people to the corresponding figures in Table III-10 for
 operation  of any combination of sites for the Metropolitan area.

         6.     Recommended Disposal Facilities.  Five solid waste  disposal
 facilities are recommended for the three county study area.   Their general
 locations and service areas are shown in Figure III-3.  The following is  a
 general description of  the area in which the site should be located and the
 area which the site will serve.

_Site Number 1,  a  sanitary landfill in the vicinity of the intersection of Interstate
 80 and U.  S. Highway 50, to serve  central and western Sarpy County, south-
 west Douglas County, and southwest Omaha.

 Site Number 3,  a sanitary landfill in the vicinity of 120th and Fort Streets
 in Douglas County to serve west Omaha and northwestern Douglas County.

 Site Number 5,  a sanitary landfill west of Lake Manawa in Pottawattamie County
 to serve Council Bluffs and southwestern Pottawattamie  County,  Bellevue and
 eastern  Sarpy County and Omaha.

 Site Number 1 f  a sanitary landfill north of Dodge Park in the  northeast corner
 of Douglas County to serve north Omaha, northeast Douglas County,  and
 northwest Pottawattamie County.

_Site Number 8,  a sanitary landfill near Hancock, Iowa to serve eastern
 Pottawattamie County.

 The three  potential facilities under consideration which were  not selected
 were eliminated for the following reasons;

         Site 2 .   Site 2 is the existing sanitary landfill immediately east
         of the Mormon Bridge in Pottawattamie County.  Site 2, rather
         than Site  7, would have been selected if it were not for its
         future  questionable accessibility and the problems which might
         be encountered in conversion from private to public operation.


                                 ni-45

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This selection would have been made even though most
of the vehicles using the facility would be required to pay
toll bridge fees in addition to disposal fees.

It is expected that the access to Site No. 2 will be appreciably
changed by the completion of Interstate 680 and cause the site to
become uneconomical because of extended haul distances and
times.  This site is privately operated and as  such,  fees are
necessarily higher than those of a non-profit,  tax exempt or-
ganization.

If the accessibility of Site 2  were to remain unchanged and
if it could be operated by  a public agency with  the resulting
fee reduction,  then the site  should be selected in lieu of  Site
No. 7.  Comparison  of simulations No. 52 containing Site No.
2 and No. 98 containing Site No.  7, which rank 5th and 9th
respectively in Table III-3,  shows that the savings to the
community would be  approximately 1. 7%.

Site 4.  The  City of Omaha recently converted its incinerator
facilities  at Site No.  4 to  a transfer station.   Transfer stations
have been discussed  previously  and were shown to be unecono-
mical under  the minimum design standards assumed and
therefore have not been recommended as part  of this system
of solid waste  disposal facilities.

The existing transfer station at Site No.  4 is presently
equipped to handle approximately 100 - 120 tons of refuse
per day and remains open 7  days a week.  Referring to
Simulation No.  100 ranked No.  2 in Table III-3, it is seen
that with a transfer fee of $1. 08 per ton($2. 33-$l. 25 Disp.  =
$1. 08 trnsf)  which is  based  on a minimum of 420 tons per day,
the transfer  station would receive  769 tons per week or an
average of 110 tons  per day, a  quantity less than that neces-
sary to make the station self supporting.   Examination of
Simulation No.  100 reveals  that less than 8% of the tons  of
waste would  appear at Site No.  4.  The area served  by the
transfer station is nearly  fully  developed and waste genera-
tion is expected to increase  only slightly  so that it becomes
apparent that Site No. 4 would never become self-supporting
and would require a continued subsidy.  A more complete dis-
cussion of transfer stations  is presented in Part III.D. 1.

Site 6 .  This site was recommended by people interested in
this solid waste disposal study.  It was subsequently tested by
site selection criteria and by the simulation process and
found to be unsatisfactory.  Access to the site is through
residential areas which would create traffic problems in these
areas.  The  most logical  combination of facilities which would
include Site No. 6 would be  Sites Nos. 3, 6 and 7. This com-
bination does not adequately serve western Sarpy County or
                          ni-46

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         western Pottawattamie County and with this combination of
         sites, Site No. 6 would receive 65% of the total waste
         quantity.  The land available  for filling at Site  No.  6 is
         approximately 90 acres out of a total of 120 acres, and
         with the site  receiving 65% of the waste it would last only
         3 to 5 years.  Simulation No. 95 containing Sites Nos. 3,
  »       6 and 7 ranks 20th in "Total Community Cost"  in Table
         III-3.

An important part of the site selection process  was to determine if a site or
a combination of sites would be properly located and of  adequate  size to
serve the future requirements of a growing population in the expanding
communities.  The map showing present and future land use (Figure III-3),
and the solid waste quantity distribution made by the computer in the econo-
mic  simulations were used to determine if there was a reasonable relation
between the land area served by a site and the measured quantity of waste
a site would receive.  The developed land areas served  in 4  different site
combinations for the year 1968 were determined by planimeter.  The indivi-
dual areas for each combination were converted to a percentage of the total
area and compared to the percentages of solid waste received at  the sites
in the economic simulations.   In all cases in the four combinations of sites
used, the pe-rcentage figures agreed within 2%.  This close  agreement es-
tablished the basis for predicting future annual  site use  and aided in the
determination of total land required at individual sites for the particular
combination of sites being considered.

Annual  site use for each year of the design period 1970  - 1995 was deter-
mined by multiplying the  annual increase in the  quantities shown  in Table
11-24 by the predicted percentage of solid waste received at a site during
that year,  and then adding that  result to the previous years quantities with
1968 as the base year. The predicted percentage of facility use each year
was  assumed to vary uniformly from  1968 to 1995.  The percentage of use
in 1968 was taken from the economic simulations.  The  percentage of use
in 1995 was determined by planimeter from the  map (Fig. Ill-3) showing
future  land use.
                                    IH-47

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         7.      Recommended Disposal Fees.  Solid waste disposal fees should be
 set to provide the revenue required to make the system of facilities completely
 self supporting.  In Section D. 4. f. of this Part III, the costs of operation are
 shown.  Four critical years are analyzed:  the first year;  the fourth year,  when
 the volume is reduced  due to the expected reduction
in Special Tree waste;the average year and the final year.   The fourth year is
 critical.  When these fourth year operating costs are added to the Debt Service   *
 Reserve for  that year,  as shown in Section D. 4.h. ,  the total required revenue is
 equal to $1. 32/ton.  This is 8£ per ton higher than the first year.  We  recommend
 the initial fee be based on the fourth  year requirement and that the fee be rounded
 off to an even $1. 40.  The actual fee to be charged will be based on a new estimate
which  must be prepared after the actual final conditions are known.   For purposes
 of this report a fee of $1. 40 per ton is used.   Under the estimated condition,
 this  fee would bring in  a  surplus during the first few years.  This surplus  could
 be placed into a reserve  to be  used as coats of operation increase due to inflation.

 After the fourth year, the unit costs  are  reduced due to the increased tonnage.
 It is entirely possible that a fee based on the fourth year cost may be adequate
 for several years after that time.

We recommend the following schedule:

                          Recommended Fee Schedule

                    Basic fee                           $1. 40/ton
                    Minimum  fee                       $1. 00
                    Private autos and station wagons    No charge

Automobiles,  if not  adequately provided for,  create  problems  at a sanitary
 landfill.  They are definitely a nuisance and danger if permitted to unload at
the "working face" of the landfill where trucks and heavy equipment are operating.
 Fata] accidents  involving people inexperienced in landfill operations have occurred
in the; working area  of a landfill.  Automobile  drivers and  juvenile occupants would
substantially increase the possibility of such accidents.  In addition, autos often
interrupt landfill activities because of their inability to negotiate soft, wet  ground
and their susceptibility to tire failures.   The amount of material delivered in
automobiles is very minor.  In Part II, it was shown that automobiles delivered
only 1% of the volume and only 0. 5% of the tonnage whereas they represented
 15%  of the traffic.  For these reasons and because automobiles will often appear
at a  sanitary landfill when it is closed, special facilities should be made available
to them.

These  special facilities should include large containers exterior to the landfill
proper, and access  by hard surface roads.  The elimination of any charge  for
these facilities eliminates the need of a fee collector and the facilities permit
normal landfill operations to proceed without the problems caused by automobiles.
                                      111-48

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The additional revenue produced through the minimum fee is almost exactly equal
to that lost through the free service offered to private automobiles.

Of the  5 recommended sanitary landfill facilities, Sites 1 and 8 would initially
operate without scales.   At these 2 sites,  a different  fee schedule equivalent to
a disposal fee of $1. 40 per ton should be established.   We recommend the
fallowing:

                       Foe Schedule Sites  1 and 8 Only

        Minimum fee                           $1. 00
        Pickup trucks (without sideboards)      Minimum charge
        Light trailers                           Minimum charge
        Packer trucks                           $. 55 per CY of rated capacity
        Private automobiles and station wagons  No  charge
        All other vehicles                       $. 35 per CY of waste
                                     111-49

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E.	SITE DEVELOPMENT

         1.      Development of a Flat Site

                a^.      General.  Flat land is generally suitable for development
using multiple layers of waste.  The cover material can be taken from the land
in a cut and cover type operation.  Site 5 will be used as an example in this       *
discussion.

                b_.      Amount of Land Required.  The amount of land required
depends on the amount of waste and the depth of fill, plus  additional land for roads,
setbacks, sight  screening and landscaping and operational spaces.  It is assumed
that the land acquisitions will require purchasing full parcels of land which would
be not less than 40 acre increments.  Therefore, it may be necessary to make
adjustments in order to take an even parcel.

The amount of cover dirt available within a flat site is  generally dependent upon
the depth of the water table.   The water table at Site 5  is normally 10' to 15'
below the ground surface.  Excavation of the site to a depth of 7. 3' will provide
the necessary cover dirt for 3-8' layers of waste, a final cover of 3 feet, the
site screening berms around the site, and road grading.

It is estimated that 20% additional land will be required for roads,  setbacks,  sight
screening, etc.  The total land purchase  is estimated as follows:

                       (1)     Land for filling

                                     9,770 ac. ft. -;-  24 ft.  =  407 acres

                       (2)     Roads, etc.

                                     407  acres x 20%        4-   82

                                            Subtotal           489

                       (3)     Less land for even parcel
                                 purchases

                                 Total Land to be Purchased

Based on a purchase of 480 acres, it was assumed the  land would consist of
3 quarter-sections.

                —•      Initial Development of the Site. Before any operations
can commence,  the site must be designed and developed.  It is recommended
that the initial development be done by a Contractor following plans and specifica-
tions prepared by an Engineer.  The initial development would consist of the
following items:


                                    IU-50

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                        (1)     Scale house,  gate house and scale equipment.

                        (2)     Equipment and personnel facilities.

                        (3)     Agency headquarters.

 *                      (4)     Water supply and mains.

                        (5)     Fencing.

                        (6)     Roads and drainage .

                        (7)     Grading and landscaping.

                        (8)     Yard and street lighting.

In the cost estimate, the initial site development at Site 5 is estimated to cost
approximately $162,500.  Some of the initial site development is shown in
Figure III-4 which illustrates the development of a flat site into a sanitary landfill.

The items listed above are self-explanatory except for the grading and landscaping.
One major grading item would be the construction of a sight screening berm
around that part of the site which will be filled first.  As filling progresses, the
berm will be extended.  The purpose of the berm is to completely screen the
site operations  from view from the road.  It will also act as a windbreak to aid
in litter control.  The berm should be planted to grass  or other suitable ground
cover.  The berm and the area between the berm and the property line should be
landscaped with trees and shrubs.  The construction of the berm and the land-
scaping are necessary parts of the entire operation and add substantially to
public acceptance.   The expense of these items are minimal when compared to
the operational  cost.

                d.      Operation of the Site.  The amount of earth needed for
daily cover, final cover, berms and roads is approximately 5  1/2 million cubic
yards over a period of 26 years.  Taking this earth from the fillable area requires
a cut of approximately 7.3'.

Starting at Elevation -  7. 3 ft. and adding 8 ft. of waste and 8 inches of cover for
each lift,  the approximate levels for the fills would be as follows:

        Lift           Bottom           Fill            Top

        First          -  7. 3            +8. 7      =      +1.4
        Second        +1.4            +8.7      =      + 10.1
        Third         +10. 1            +8. 7      =      + 18. 8
        Final Cover   +18.1            +2.3      =      + 21.1
                                      III-51

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 Tin- laudfilling can start at Elevation - 7. 3 in the area where the initial devel-
 opment earth was excavated.  As this space is being filled, the cover dirt
 required is excavated from the immediately adjacent  space,  thus  creating
 additional area with a bottom elevation of  -1. 3.

 The filling should be from the bottom of the lift with trucks dumping at the  foot
 of the active face and the dozer compacting and pushing the waste up from the     »
 bottom.   Bottom dumping has  advantages over dumping at the top  and pushing the
 waste down the slope.

 The active face should be between 150 and 200 feet wide depending on the traffic.
 As the first lift is filled  over an area approximately 200' wide  x 1,000" long, the
 top surface of the first lift becomes available for the  second lift.  When this
 first 200' x 1,000' pass of the first lift is complete, the second lift should start.
 The second lift can be filled to an elevation of  10. 1'.  It starts at  the same point
 the first lift  started and  can cover the same 200' x 1,000 except for maneuvering
 room needed around the  edges.  By the time the second lift is complete,  to the
 extent it has covered as  much of the first lift as possible,  the filling can return
 to the -7. 3' elevation in  the space excavated while the first and second lifts were
 being filled.   This second pass on the level of the first lift will widen the top
 surface of the first lift to the extent that additional area is available for the
 second pass of the second lift.  Once this second pass of the second lift is com-
 pleted, the third lift can be started on top  of the second lift.

 The process of building lift upon lift and then returning to the bottom to widen
 the base is necessary to build up to the top of the third lift as soon as possible.
 It is at this (+18. 8') level that the final earth cover is placed.  This cover material
 amounts to approximately 1/3 of the total earth moved. Therefore, it is desirable
 to reach the top as soon as possible so excavated material from the -7. 3' level can
 be brought directly to the +18. 8 level without rehandling.

 In Figure III-4, the site operation is shown. The first view  shows the site after
 the first few  months of operation.   The first pass of the first lift has been com-
 pleted.  The  first pass of the second lift is in progress while additional cut is
 being made on the -7. 3' level.

 The second view  shows the site after approximately one year.   The +18. 8'  level
has been reached.  The operation from this stage until the completion of this
 area  consists of widening the base and adding additional lifts on top until the
 area has all been filled to elevation +18. 8'.

 The third view shows this area filled and the operation moved to the adjacent
 area on the opposite side of the fill road.

 The fill road leading from the scale and entrance area to the fill area would be
 built  in the initial development to an elevation of +10.  1.  As the third lift is
placed, the road would be raised in the fill area,  to reach  the top of the third
 lift at elevation +18. 8' for access to this level.
                                      111-52

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         2.      Development of a Hilly Site

                 a.      General.   Site 3 is used as an example in this discussion.
 The land in this area is hilly containing one large gully which could be developed
 using typical gully filling methods.  Cover material can be taken from the gully
 bottom and sides in a combination cut and cover and borrow type operation.
 •
                 b_.      Amount of Land Required.  The amount of land required
 depends on the  depth of fill plus additional land for roads, setback, drainage,
 sight screening and landscaping and operational space.  Since the gully is  irregular
 in shape it will be necessary to purchase the parcels of land which  surround and
 contain the gully.  The depth of fill varies from point to point within the gully.
 The volume that can be filled is determined by laying out the final top surface
 contours and computing the volume between the original ground and the final
 cover.

 The site illustrated in Figure III-5 shows the necessary land which is approximately
 200 acres.  The principle gully on the site is shown filled to a top elevation of 1200
 ft. (MSL),  and can contain 4350 acre feet.

                c^.     Initial Development of the Site. Before any operation can
 commence, the site must be  designed and developed.  The procedure and items
 of work would be similar to that described for  a flat site,  except the  details of
 the design will be completely different.  The major site screening can be accomp-
 lished by landscaping.  During  the initial years while the landscaping was  maturing,
 the operation would be hidden from view deep in the gully.  An initial berm would
 be constructed across the lower end of the site  and landscaped, but this  berm would
 be limited in length  and height.

 Although the berm construction would be less than that shown  for the  flat site, the
 temporary road construction  would be more extensive.  Roads would  be  required
 for access from the permanent perimeter road to the active face of the  fill.

 Details of the site development were not worked out to the extent shown for the
 flat site.  The costs for initial development were estimated  to be $112, 000.

                d.     Operation of the Site.  The earth for cover can be taken
 from the bottom and side walls  of the gully as the work progresses.  The amount
 of cut must be calculated to cover the many lifts which will be made plus the final
 cover on top of  the completed fill.   The calculation must be  based on  the final
 design which will vary depending on which specific site is  selected.

 The great depth of fill in this type  of  site  has a distinct advantage over a site
filled to a 10 to  15 foot depth  which is commonly used,  due to  a reduced volume
 required final cover material.  The final  cover is recommended to  be approxim-
ately 3 feet thick compared to a daily cover of approximately 8 inches thick.   If
a single lift were used it would require a  final cover.  If two lifts were  used the
final cover requirement per lift would be  cut in half.  Similarly, each additional
lift reduces the  percentage of final cover  per unit volume filled.  This is also true
for the three lift flat site proposed for the northeast area.

                                      HE-55

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LEGEND
             EXISTING PROPOSED
     CONTOUR —"M-	it"	
       FENCE
 PROPERTY LINE
        ROAD
    RESIDENCE   •
       TREES
DRAINAGE DITCH
  JINITIAL  DEVELOPMENT
                                  III-5 6

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j FINAL DEVELOPMENT
                          TYPICAL HILLY SITE
                    HI-57                 FIGURE ur - s

-------
Filling should start near the upper end of the gully and be worked down some
convenient distance.  The second lift should be filled on the top of the first, and
the third on top of the second in a manner similar to the filling of the flat site.
Filling from the upper end of the gully allows  surface water in the form of rain     *
or snow to drain away from the fill.  This is a very important feature which must
be followed in this type of an operation.  When necessary, the filling  can  resume
at the first level and be continued for another distance to give working and
maneuvering room on the second and higher lifts.  The process of extending the
lowest lifts and then extending each higher lift should be repeated until the final
contour or top  of the completed fill is reached.
F_.	FINAL USE AND INTERIM USE OF SANITARY LANDFILL SITES

Once completely filled,  sanitary landfill sites  can be used for a variety of purposes.
It is necessary to understand the nature of a fill site when planning its use.  The
sites will settle over a period of time; therefore, improvements built upon solid
waste fills must be  either compatible with the  settlement or the foundations
must penetrate the fill into firm ground below  the fill.  Many structures have
been successfully built on fills using light buildings and floating foundations, and
many heavy structures have been built on piles penetrating through the fill.

The landfills will produce some gasses, normally methane,  due to the biological
decomposition of the organic material in the fill.  These gasses under certain
conditions are toxic and explosive. Normal landfill conditions permit harmless
concentrations of these gasses to escape to the atmosphere.  Many structures
and other improvements have been successfully constructed on sanitary landfill
sites where the problem of gasses has been properly provided for.

Generally,  completed landfills have been used for open space purposes such as
parks, golf courses, and recreation areas.

Normal improvements associated with these uses such as pavements, shelter
houses, etc. ,  can be designed for landfills.  Landfill sites can and have been
used for agricultural purposes after completion.

A well-planned arboretum could be a pleasing and interesting addition to a
community,  especially in the future after many forrested areas may possibly
disappear.  A  landfill site, if properly handled, could be well suited to this use.

The interim use of sanitary landfill sites could be anything of a temporary
nature compatible with the  landfilling and with activities and  land use in the
surrounding area.  A large  site such as the one recommended in the area of
Lake Manawa would have approximately half of its area or 240 acres available
for other uses for about 10 years.

Planners in the community are cautioned to take special notice of the rate of
completion of finished filled land.   When a landfill is conducted using only one
or two lifts, the rate of completion of filled land is greater than the landfills
contemplated in this report, where more lifts  are contemplated.   They may
wish to concentrate efforts on the  land not being filled for the first 10 years,  and
then devote their efforts toward use of completed portions.

                                   Ill-58

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    PART FOUR - ORGANIZATION FOR SOLID WASTE DISPOSAL

 A.       GENERAL.   The recommended organizational structure for the
 disposal of solid waste is a single, non-profit,  public agency.  This agency
 would be formed for  the purpose of operating and/or managing all public
 solid waste disposal  facilities in the three county MAPA area,  as one coordi-
 nated activity, in accordance with a master plan for area-wide solid  waste
 disposal.  It would operate for and on behalf of all of the member municipali-
 ties for their mutual benefit.

 Each member would  agree to the master plan and pass any ordinances or
 regulations necessary to implement the  plan and to grant to the agency
 exclusive operating authority within their jurisdiction.

 Fees would be charged at all agency facilities,  for disposal services.  These
 fees would be uniform at all facilities, non-discriminating,  and adequate in
 amount to produce the necessary revenue to make the entire disposal opera-
 tions self-supporting.

 The purchase of land, capital improvements to the land and initial comple-
 ment of equipment would be paid for with the proceeds of revenue bond issues.
 The user fees would  pay for the bond debt service,  debt  service reserve,  opera-
 tion and maintenance, equipment replacement,  site improvements, miscellane-
 ous and incidental expenses, management and overhead.

_B.	COLLECTION  OF SOLID WASTE .  In following paragraphs  of this
 Part  of the  Report, the  legal status  of the agency is described  and a suggested
 form of agreement to create the agency  is presented.  This agreement in-
 cludes the necessary authority for the agency to enter the field of solid waste
 disposal.  It also includes  authority to provide  solid waste collection services.
 The collection services  contemplated  at  this time are minor in nature and are
 restricted to  the rural communities in eastern  Pottawattamie County, where
 some form of formal collection service  will be desirable to make a single re-
 mote sanitary landfill site  economical.  This was discussed in Part III of this
 report.

 The scope of this report is limited to disposal  problems and specifically ex-
 cludes collection matters; however some discussion of collection  of rural com-
 munities waste was necessary and therefore included.   The Agency probably
 will wish to study collection problems in the future  and it is likely they will
 find that great savings can be  made  by organizing an area wide collection
 service.  For this reason the  Intergovernmental Agreement (Document IV-1)
 creating the recommended Agency includes the power to collect and dispose
 of solid waste, should the Board wish to include collection service.

_C_.	LEGAL STATUS  OF THE AGENCY.  The Agency may be formed under
 provisions of Chapter E8E of the Code of Iowa entitled "Joint Exercise of
 Governmental Powers"  and  provisions of Chapter 23, Article 22  of the Statutes
 of Nebraska entitled  "Interlocal Cooperation Act. "

                                   IV-1

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DOCUMENT IV - 1, Page 1

 INTERGOVERNMENTAL AGREEMENT CREATING THE OMAHA-COUNCIL BLUFFSMETROPOLITAN
                               AREA SOLID WASTE AGENCY
 By virtue of this agreement made and entered into by the undersigned, there is hereby formed the
 Omaha - Council  Bluffs Metropolitan Area Solid Waste Agency, hereinafter called the Agency,
 consisting of the elected representatives of the governing bodies of certain cities, towns, villages
 and counties in the Omaha - Council Bluffs Metropolitan area of Iowa and Nebraska. The cities,
 towns,  villages and unorganized portion of the counties are hereinafter called Municipalities.

 WITNESSETH:

                                             I

                                        AUTHORITY
 The Municipalities enter into this agreement under and by virtue of the power to do so granted by
 Chapter 28E, Code of Iowa, 1966; and by Sections 23-2201 thru 23-2207, Revised Statutes of
 Nebraska 1965.
                                         PURPOSES

 The purposes of the Agency are as follows:

 1.  To provide for the economic and sanitary collection and/or disposal of solid wastes produced
     or generated within each member municipality.

 2.  To cooperate with local, State and Federal public health agencies in preventing the contam-
     ination and pollution of the  land, water and air resources of the area, through the control,
     collection and disposal of solid waste.

 3.  To engage such employees and provide offices, equipment, machinery, buildings and grounds
     as are necessary to adequately perform the functions of the Agency.

 4.  To contract with member cities,  towns, villages and counties and with public  or private
     persons,  firms or corporations for the collection and/or disposal of solid waste, and collect
     payment for such services, and to receive and expend State, Federal  and private grants and
     other monies which may be made available, to the extent permissible under applicable State
     and  Federal laws, and under the rules hereinafter set forth.
                                     ORGANIZATION
  1.   Membership in the Agency shall consist of a representative from each participating municipality,
      or his designated substitute, which substitute shall be approved by the body he represents.
      The representative shall be an elected official of the municipality he represents.  Each partici-
      pating municipality shall have one vote for each 50,000 population or fraction thereof, residing
      in the governmental  jurisdiction he represents.  Such population shall be ascertained from the
      most recent Federal Census for that jurisdiction.

  2.   The governing body shall be designated the Agency Board, hereinafter called the  "Board",
      consisting of the member representative from each city with a population of 20,000 or
      greater; the member representative of each county; and one additional member representative
      from each county who shall represent all  of the incorporated cities, towns,  or villages in that
      county not individually represented on the Board.

  3.   Each.member  of the Board shall have one vote for each 50,000 population or fraction thereof,
      residing in the government jurisdiction he represents.  Such population shall be ascertained
      from the most recent  Federal  Census for that jurisdiction.


                                            IV-2

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  Document IV-1, Page 2


 4.   A quorum shall  consist of a majority of the entire Board membership, regardless of the number
     of votes held by each member present.

 5.   The Chairman and the Vice-Chairman of the Board shall be elected  by majority of Board
     membership and shall  serve for a term of one year or until their respective successors
     in office are  chosen.  The incumbent in each said office may succeed himself.

 6.   The Board shall hold at least  one meeting during each quarter of  the year on dates and at
     places which shall be determined by the Board.  Special meetings may be held at the call of
     the Chairman,  Vice-Chairman or majority of the membership of the  Board.

 7.   The Board shall hire a  Director and such other supervisory,  clerical,  and other personnel as
     are necessary to carry out the functions of the Agency.  The Board shall  fix their compensation
     and benefits, and shall approve all personnel rules and regulations pertaining thereto.

 8.   The Director  shall be  the Secretary and Treasurer of the Agency and shall have the authority,
     duties  and obligations normally associated with these offices, including but not limited to
     the receipt and disbursement  of funds and the preparation and submission of  quarterly and
     annual financial reports to the Board.

 9.   The Board may  employ legal counsel, who may be a paid employee of one of the members,
     and who may receive  compensation set by the  Board for the performance  of his duties.

10.   A meeting of the  entire Agency membership shall be held annually at a time and place
     determined by the Board and  at such other times  as the Board may direct  or when there is a
     call for a meeting by  a majority of the  membership.

     The Chairman and Vice Chairman of the Board shall be the  Chairman and Vice Chairman of
     all Agency membership meetings.

11.   The Board shall prepare and present to the Membership for approval  the "By Laws of the
     Agency".  A 3/4 vote shall be required for approval.  The Board or the  membership may,
     present,  at any meeting,  amendments to the By-laws.   A 3/4 vote of the membership  shall
     be required for approval of changes to the By-Laws.

                                            IV

                                        DURATION
 1.   It  is the intention of this agreement that the Agency be a permanent organization.  Additional
     municipalities may be added to the membership of the Agency upon a three-fourths vote of
     all of the  members of the Board.

 2.   In the event an additional municipality shall apply for membership in the Agency and said
     application is considered and approved by the  then existing Board, then said municipality may
     be added to the membership, provided that said additional municipality as a condition of
     membership  agrees to abide by the terms of this agreement as set out herein and possess legal
     power and authority to do so.

                                             V

                                         POWERS
 The Municipalities delegate the following powers to the Agency and Board:

 1.   To provide solid waste  disposal facilities and service  for all  member municipalities and the
     public within the  general geographic area of the member Municipalities.

 2.   To provide solid waste  collection and disposal service to those member municipalities requesting
     such service, within the limits authorized by law.
                                          IV-3

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  Document IV-1, Page 3


 3.  To receive funds from member Municipalities as payment for providing collection and disposal
     service.  However, in lieu of receiving such funds from member municipalities, it shall have
     the power to bill  individuals directly for payment  for collection and disposal services and to
     receive such payments, for and on behalf of the municipalities where such direct charging of
     fees is authorized  by law, and where the member requests such billing.

 4.  To contract with all levels of government, other public agencies, private agencies and private
     individuals,  toward the accomplishment of the  stated purposes of the Agency, within the  limits
     authorized by law.

 5.  To establish a schedule of fees to be collected   from all users of the Agency's disposal facilities,
     provided however  the schedule of fees shall be uniform to all users.

 6.  To hire employees, fix their compensation, benefits, personnel rules and regulations, and
     terminate their employment.

 7.  To purchase, lease, receive as gjfts or donations,  or otherwise acquire all land, buildings,
     equipment and supplies as necessary to carry out the functions of the Agency, and to dispose
     of the same.

 8.  To make or cause to be made studies and surveys necessary to carry out the functions of the
     Agency.

 9.  To contract with and compensate consultants for professional services including  but not limited
     to architects, engineers, planners,  lawyers, accountants,  rate specialists, and  all  others found
     necessary to the stated purposes  of the Agency.

10.  To issue revenue bonds for the purchase of land and equipment  and erection of buildings and
     other improvements, and to provide for their retirement, within the limits authorized by law.

11.  To prepare and recommend to member Municipalities local ordinances  governing refuse storage,
     collection,  transportation and disposal, regulation of private collection haulers, land use
     regulations,  sanitation, burning of private or public wastes, incineration  standards and such
     other regulations as may from  time to time  be required.

12.  To exercise any and all powers relative to the efficient collection and disposal  of solid waste
     available under then existing  laws to each member Municipality.

13.  To prepare by-laws, rules and regulations, fee schedules,  and entrance and termination forms
     and procedures for membership in the Agency.

14.  To provide for a system of budgeting, accounting, auditing and reporting  of all  Agency funds
     and transactions, for a depository, and for the  bonding of employees.

15.  To consult with representatives of Federal, State and local agencies, departments and their
     officers and employees and to contract with such agencies  and  departments.

16.  To accept gifts, grants, or loans of money or other property from the United States,  the states
     or any person,  corporation or other entity for Agency purposes,  and to enter into any agreement
     required in connection therewith, and to hold,  use, and dispose of such money  or property  in
     accordance with the terms of the gift, grant, loan or agreement relating thereto.

17.  To exercise any and all other powers consistent with the  stated purposes of the Agency available
     under then existing law to each  member Municipality.
                                            IV-4

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 Document  IV-1,  Page 4

                                            VI.

                    TECHNICAL COOPERATION FROM MUNICIPALITIES

The Municipalities agree to respond to reasonable requests to make local records available to the
Agency staff and  its consultants or employees for the purposes of this agreement, and to assure that
engineers,  architects  and consultants hired by the  Municipalities release materials, data and other
pertinent items paid for by  public funds, to the Agency staff to  aid in  the efficient and effective
accomplishment of such purposes.
                                       FINANCING
1.  The Board shall prepare a budget based on calendar years for the operation of the Agency to
    be adopted in June of the year preceding the budget year.

2.  The Board shall request each Municipality to provide in its  budget for its share of the Agency
    budget.

3.  The Board shall annually adopt a percentage formula, based on population, as shown in the
    last completed Federal census, for the purpose of allocating the portion of the Agency  budget
    each Municipality will provide.

4.  The share of each budget from each Municipality shall  be due and payable to the Treasurer
    of the  Agency in quarterly payments to be made within 30 days after the beginning of the
    quarter of the Agency's budget year.

5.  Special appropriations shall  be made by the parties hereto for funding the operation of  the
    Agency prior to the establishment of the  budget  cycle.

6.  Any special or budgetary appropriation adopted  by the  Agency  shall be a membership
    requirement of each and  every Municipality and shall upon the Municipality's contracting
    with the  Agency therefore constitute a legal liability on the part  of such Municipality.
    The failure of a Municipality to pay over to the Agency the allotted share of an Agency
    budget may be considered a  momentary withdrawal of that Municipality and a default of
    this Agreement.

                                           VIM.

                    SUSPENSION OF VOTING RIGHTS AND SERVICES

During a period of delinquency by a Municipality in the payment  to the Agency of its share of a
budget and before  such delinquency is determined a voluntary withdrawal, such Municipality shall
not be entitled to the services of the Agency, nor shall the  Municipality be entitled  to vote on
matters coming before the  Board, unless such  delinquency shall  be waived for voting  purposes by a
three-quarters vote of the  remaining members of the Board.

                                           IX

                                      DISSOLUTION
     In the event of the withdrawal of any Municipality from the Agency such withdrawing
    Municipality  shall be entitled to a pro-rota share of the value of the real and personal
    property of the Agency.  Such share shall be  calculated as the  percentage of the then value
    of said property based on the ratio of the funds the withdrawing Municipality has provided to
    the Agency during the period of this agreement to the sum of all funds provided by all Munici-
     palities.  Funds for the payment of the pro-rata share of such property value shall be provided
     for in the next succeeding Agency budget cycle and shall be payable within six months of the
     beginning of the budget year in which the  item appears.   A withdrawing Municipality  may
    waive its pro-rata share of any real or personal property in the  possession of the Agency.
                                           IV-5

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 Document IV-1, Page 5


2.  The Agency shall be completely dissolved and this agreement terminated only upon the
    affirmative three-quarters majority vote of the Board.

3.  In the event of complete dissolution of the Agency, any real or personal property shall be
    sold and the proceeds prorated among the  Municipalities at the time of dissolution on the
    basis of the sum of the portions of the budget for the  Agency provided by them for and during
    the period of this agreement.  The current budget year shall be used as one of the years in
    the calculation  if all Municipalities have made their proper contribution.  If all members
    have not made  their proper contribution, the balance remaining of funds collected during
    the current year shall be refunded to the contributors before determining the value of the
    assets of the Agency at dissolution, and said year shall not be used in calculating the  shares.

4.  In the event the Agency has acquired a debt thru the issuance of bonds or loans or otherwise,
    and  such debt is still outstanding, and unpaid, no member may withdraw or in any way terminate,
    amend, or modify this agreement in any manner to the detriment of the bond holders or holders
    of notes or other instruments of debt.

                                            X.

                   MANNER OF ACQUIRING  AND HOLDING PROPERTY

 1.  The  Board may lease, purchase, or acquire by any other means, from  members or from any
    other source, such real and personal property as  is required for the operation  of the Agency
    and  the carrying out of the purposes of this agreement. The Board shall maintain title to all
    such property  in the name of the Agency and shall require the Secretary to  maintain an
     inventory.  Property, materials and services shall be acquired or disposed of only upon a
    majority vote of a quorum attending a duly called Board meeting, provided however, that
    by the same vote,  the Board may authorize the Director to expend such funds as the Board
    may direct for other authorized purposes of the Agency.
                                            IV-6

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These two state provisions are similar to the typical Joint Powers Act found
in many state codes.  They provide, in part,  that any governmental subdivision
may cooperate or contract with another subdivision, or jointly perform any
service  or exercise any power which they individually have the power to do;
or they may form a separate agency for this purpose.  These same two
legislative provisions are the legal basis  upon which the Omaha-Council
JUftffs Metropolitan Area Planning Agency was formed.

A proposed form of an intergovernmental agreement to  create  and operate
the agency is included in this Part IV of the report as Document IV- 1.

This agreement is applicable to cities,  towns and counties in Iowa and cities,
villages and counties in Nebraska.  Hereinafter cities,  towns,  villages and
counties are referred to as  "Municipalities".

P.	MEMBERSHIP. It is essential to the plan, as  proposed,  that the poli-
tical jurisdictions in which sanitary landfill sites are located be members of
the agency.  This includes Council Bluffs, Omaha,  and  the counties of
Pottawattamie,  Douglas and Sarpy.  It would be desirable if  all of the muni-
cipalities in the Study Area executed the agreement.

_£_.	FORMATION OF THE AGENCY .  It is recommended  that the Agency
be established as  an independent entity, whose membership would be comprised
of one representative  from each participating municipality.  The representative
would  be one of the elected officials of the municipality.  The Agency would be
governed by a Board of Directors  comprised of the  representative of the major
cities; the  counties; and 3 additional representatives,  each of which would re-
present the smaller cities, towns or villages in each of the three  counties.  In
voting matters concerning the entire Agency and/or the  Board,  each represen-
tative  shall have one vote for each 50,000 population or fraction thereof resid-
ing in  the jurisdiction he represents.

With the membership  consisting of elected representatives, direct lines of
communication between the Agency and the municipalities is  established and
the following benefits  realized;

         1.      The Agency would function with real authority  since individual
members would be an elected official who would represent and speak directly
for his respective  city,  town and village councils,  and county boards.

         2.      Feedback to the member jurisdictions would be accomplished
by having direct representation on the Board.

         3.      Limiting the Board membership in the manner described would
prevent the membership of the Board from becoming too large to function
effectively as  a policy making body.

         4.      Weighing the  vote of each member on a population basis would
provide a fair method of recognizing the population differences between the
member jurisdictions.

                                     IV-7

-------
 The length of the term of membership on the Board should be determined when
 the By-Laws  for the Board are initially drawn up.   Provisions should be made
 to assure  continuity on the Board, taking into account the variations in the
 ordinances of the member jurisdictions regarding length of office of elected
 officials.

 The broad purposes of the Agency as outlined in the proposed Agreement are
 as follows:

         1.     To provide for the efficient and economical,  collection and
 disposal of solid waste produced or generated within the Study Area.

         2.     To promote through good practice,  effective means for re-
 ducing or  preventing the contamination and pollution of the land,  water and
 air resources of the Study Area.

         3.     To provide for a self-supporting, independent organization,
 equipped with sufficient manpower and facilities to adequately perform the
 purpose of the Agency.

 A proposed organizational chart for the Agency is shown on Figure IV-1.  This
 chart indicates the  flow of authority from the elected municipal and county
 officials, to the Agency Board and the Director.

 The director would be responsible for the administration and operation of
 the Agency, under policies adopted by the Board. This is  a top
 level position requiring experience in public works  management,  personnel
 management, engineering and public financing.

 The assistant director should have qualifications similar to that  of the director.

 Professional  staff services such as legal, engineering,  planning and research
 could be provided by full time employees or  by consultants.  This determina-
 tion should be made by the Board  and the director  in the development of the
 work program for  the Agency.   The Agency may be able to utilize personnel
 employed by member communities for these specialized services.

 It is believed that the majority of jobs in the collection  and disposal divisions
 can be filled by absorbing qualified personnel from  existing municipal refuse
 agencies.  Provisions should be made to guarantee  that transferring employees
 retain their basic job benefits, including  seniority,  vacation accruals and re-
 tirement credits.

 In-service training programs should be established, particularly in the refuse
 disposal division,  to adequately train personnel at the several landfill sites
 in the methods and  procedures recommended in Part III of this report.

_F_.	OPERATION OF  THE AGENCY.  It is proposed that the Agency  be
 operated in a manner similar to a public utility, responsible to the Agency
 Board rather than  any one municipality or county.   It should have authority

                                    IV-8

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to operate independently of city limits,  county or state lines provided the city,
county or state is an Agency member.

The  Agency will be able to function most efficiently and economically if all
jurisdictions in the Study Areaare participating members.  However, this
is not an absolute necessity.  It is  possible, economically  and politically, to
form the Agency,  as it is  contemplated in these recommendations,  if only
Omaha, Council Bluffs, and the three counties of Pottawattamie, Sarpy and
Douglas join.   These are the major jurisdictions and the jurisdictions in
which sanitary landfill sites are located.

Basically, the Agency will provide  two types of service for the area; refuse
disposal and refuse collection,  as follows:

         1.      Refuse disposal - Five Agency owned or leased, managed and
operated landfill sites will be open to anyone wishing to dispose  of solid waste.
The  description and location and operation of the landfill sites have previously
been discussed in Part III.  All vehicles other than automobiles  will be charged
a disposal fee, based upon the amount of refuse delivered.  It is recommended
that  private individuals using automobiles be allowed to use the  landfill sites
without charge.  A proposed disposal ordinance has been prepared and  is
included in this part of the report as Document IV-2.

         2.      Refuse Collection - In rural Pottawattamie County, one central
sanitary landfill is recommended.  To be economical some form of cooperative
collection service should be organized.  See Part III for discussion of this
service.

In the event the Agency wishes to provide limited collection service at this
time and expanded service sometime  in the future,  the Agency may contract
with each member jurisdiction requesting this service, to  provide  refuse collec-
tion  service.  The contract would include the method of determining the actual
cost, the type of service,  frequency of service and other related items.  It is
recommended that each member jurisdiction adopt a refuse collection ordinance,
consistent with collection requirements of the Agency.   A  proposed collection
ordinance has been prepared and is included in this part of the report as  Docu-
ment IV-3.

Initially,  a problem would exist  in  providing collection service  in the unincor-
porated areas of the counties.  Statutory authority  for  county  refuse collection
is presently not available. It is recommended that county  officials request
such legislation during the next session of the legislature.  Until such legisla-
tion  is available,  it is believed that collection service  can  be  provided  to most
unincorporated areas on a voluntary basis.

G.       FINANCING.
         1.      Disposal Service.

                _a.    Revenue Bonds .  Initial capital investments and annual
operating revenue will be  required for disposal service.  It is recommended
that the initial capital investments be financed through revenue bonds.  The
                                  IV-10

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 DOCUMENT IV-2, Fhge 1

 PROPOSED REFUSE DISPOSAL ORDINANCE FOR CITIES CONTRACTING WITH THE OMAHA-
 COUNCIL BLUFFS METROPOLITAN AREA SOLID WASTE AGENCY

                                  Ordinance No.
 AN  ORDINANCE PROVIDING FOR MUNICIPAL DISPOSAL OF GARBAGE AND REFUSE; DEFIN-
 ING TERMS; PRESCRIBING RULES AND REGULATIONS THEREFOR;  REGULATING THE PRIVATE
 DISPOSAL OF GARBAGE AND REFUSE; PROVIDING FOR THE LICENSING AND REGULATION
 OF PRIVATE LANDFILL OPERATORS AND DISPOSAL SITES; PROVIDING PENALTIES FOR VIOLA-
 TION THEREOF; AND REPEALING  ORDINANCE NO.	AND ALL OTHER ORDINANCES
 AND PARTS OF ORDINANCES IN CONFLICT THEREWITH.

 BE IT ORDAINED BY THE CITY COUNCIL OF THE CITY OF                                 :
SECTION 1 .  For the purpose of this Ordinance the following definitions shall apply;

1 .1  "Agency" shall mean the  Omaha-Council Bluffs Metropolitan Area Solid Waste Agency.

1 .2  "Construction Demolition Waste" shall mean waste building materials and rubble resulting
from the demolition of building structures,  pavements and other physical  facilities.

) .3  "Garbage" shall mean the solid or semi-solid animal and vegetable  waste resulting from the
handling, preparation, cooking and serving of foods, including cans, bottles and cartons in which
it was received and wrappings  in which it may be placed for disposal .

1.4  "Person" shall mean any individual, firm, association, syndicate, co-partnership, corporation,
trust, other legal  entity having proprietary interest in a premise, or other legal entity having re-
sponsibility for an act.

1 .5  "Health Officer" shall mean (each City, Town, Village and County should  indicate who shall
be the  Health Officer who shall have responsibility for  administering and enforcing this ordinance).

1 .6  "Sanitary Landfill" shall mean a controlled  method of disposing of refuse on  land without
creating air,  land or water pollution or nuisances or hazards to public health or safety, by utilizing
the principles of engineering to confine the refuse to the smallest practical volume, and to cover it
with a  layer of earth at the conclusion of each day's  operation, or at more frequent intervals as
may  be necessary.

1 .7  "Refuse" shall mean unwanted or discarded material resulting from commercial,  industrial and
agricultural operations and from normal community activities.  Waste refuse includes in part the
following: garbage; rubbish; ashes and other residue  after burning; street refuse; dead animals;
animal  waste; abandoned vehicles; agricultural,  commercial and industrial waste; construction and
demolition waste and sewage treatment residue.

SECTION 2.   By virtue of an agreement dated            between the City and the Agency, the
Agency has agreed to provide and operate sanitary landfill facilities for and on behalf of the City,
for the disposal of refuse originating within the jurisdiction  of the City-

The sanitary  landfill facilities operated by the Agency are hereby designated as the official "Publ.ic
Sanitary  Landfill" for the disposal of solid waste  originating within the jurisdiction of the City.
No other Rjblic Sanitary Landfills are authorized; provided  however, any publicly operated facili-
ties or privately operated facilities  open to the public,  which are in existence and operating at the
time of the effective date of this ordinance may continue to operate until one year after the effec-
tive  date of this ordinance.

The Agency is authorized to establish  such rules and regulations as may be reasonable and necessary
for the  proper operation of the  facilities and to modify or amend or extend such rules and  regulations
as may  be required from time to time.
                                      IV-11

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 Document  IV-2,  Page 2

The Agency is authorized to establish a schedule of fees to be paid by the users of the facilities,
to cover the cost  of owning and operating such facilities and other expense directly related to
said facilities; provided however,  said schedule of fees shall be nondiscriminating and shall apply
equally to all  users.

SECTION 3.  All sanitary landfills within the jurisdiction of the City shall be operated in a sani-
tary,  safe and nuisance free manner,  and shall comply with all local, state and federal laws and
regulations.  In addition to other laws or regulations which may be required the following standards
shall apply:

SANITARY LANDFILL STANDARDS
3.1  Zoning.  Sanitary  landfills shall be located only in areas zoned to permit such land use.

3.2  Flooding. Sanitary landfills shall be located in places not subject to overflow of streams,
rivers, or water courses; or shall be suitably protected by levees or other control devices to prevent
overflow.  The 50 year  flood shall be used for design purposes in Urban Areas and the 20 year flood
in Rural Areas.

3.3  Sight Screening.  The site operations shall  be suitably screened by fences, earthen berms,
natural barriers or landscaping,  from view from any ground level point outside the site area that
is within  1320 feet of the filling operation.

3.4  On-Site Access Roads.  Access roads shall  be provided on the premises of the site  which are
readily negotiable by heavy and light vehicles during wet weather.

3.5  Off-Site Access Roads.   Access roads leading to the site shall be all weather roads adequate
to carry the expected traffic .

3.6  Personnel Shelter.  Suitable shelter and sanitary facilities shall be provided for personnel.

3.7  Quantity Measurements. Sites designed for disposal of refuse, at the rate of 100,000 tons
per year or greater,  shall be equipped with motor truck scales and  a record of tonnage of waste
disposed of shall  be kept.  However, the operator may at his option exclude automobiles and/or
pickup trucks and other small  vehicles from weighing requirements, provided some alternate and
suitable form or record of waste delivered in these vehicles is maintained.

Sites designed for disposal of refuse at the  rate of less than 100,000 tons per year shall  determine
the amount of refuse disposed of by weighing of loads or some other suitable method.

All sites shall determine the volume of material  filled by physical survey at time increments not
to exceed each 6 months.

3.8  Controlled Access.  Access to the fill  areas shall be limited to those times when an attendant
is on duty. Positive means shall be provided to limit the access thru the use of fence,  gates,
natural barriers or other suitable means.

3.9  Burning Prohibited.  No open burning of any kind shall be permitted at a sanitary landfill
site  at any time.

3.10 Fire Prevention.  Suitable measures shall  be taken to prevent accidental  fires at  site  including
but not limited to no smoking regulations and  regulations prohibiting loads which may be  a  fire
 hazard.   Regulations shall be posted and enforced.

3.11 Control of Fires. Suitable provision shall be made to control and extinguish fires accidentally
started.

A stockpile of cover dirt  shall be maintained near the active face  to be used  to smother fires when
necessary. Also water from mains, tanks or ponds, or suitable water wagon shall be available.
 Buildings and equipment shall be equipped with adequate fire extinguishers.

3.12  Unloading. The unloading of refuse  shall be under the general  direction of an attendant who
shall control the place of deposit.
                                            IV-12

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 Document  IV-2, Page 3

3,13  Working Face.   The working face of the sanitary landfill shall be confined enough to be
easily maintained with available equipment.

3.14  Litter.  Blowing litter shall be controlled by providing fencing near the working area, and
in addition by other fencing, berms, windbreaks, natural barriers or other methods as required to
prevent wind blown litter from leaving the working area and the general site area.  Unloading
shall be coordinated with wind direction to reduce wind blown litter.  The entire site shall be
kept free of accumulated litter by a combination of prevention and policing.

3.15  Spreading and Compacting.  Refuse shall be spread and compacted in shallow layers, not
exceeding a depth of  two feet of compacted material.  Additional layers shall be placed one upon
another until the depth of fill  has reached a predetermined height for that particular daily lift.

3.16  Daily and Intermediate Cover.  A uniform compacted layer of at least 6" of suitable cover
material shall be placed on all exposed refuse by the end of each working day. Where a com-
pleted lift is to be left for more  than 6 months before the application of another lift, the depth of
cover requirement shall be  increased to a minimum of 12" compacted thickness.

3.17  Final Cover.  A layer of suitable cover material compacted to a  minimum depth of three
feet shall be placed over the entire surface of each  portion of the final lift not  later than 3 months
following the placement of final lift.  This final cover shall be fine graded to the grades established
for the ultimate use of the site.  The graded final cover shall be planted to grass or other suitable
ground cover at the earliest reasonable time and watered and maintained to establish an adequate
ground cover.

3.18  Maintenance of Equipment.  Provisions shall be made for the routine operational maintenance
of equipment at the landfill site  and for prompt repair or replacement- of landfill equipment.

3.19  Special Materials. Special provisions shall be made to handle sewage solids, meat packing
industry waste, bulky  wastes or other special or hazardous waste, when such wastes are accepted
at a sanitary landfill.  Provisions shall include established standard  operating procedures which
shall be known to attendants and posted for public information.

3.20  Vector Control. Conditions unfavorable for the production of insects and rodents shall be
maintained at all times.  Supplemental vector control measures shall be instituted when  necessary.

3.21  Dust  Control. Suitable  control measures shall be taken to prevent a nuisance from dust.

3.22  Ground Water.   Refuse shall not be placed in locations or at elevations where contact with
ground water is likely and such contact would result in pollution of  ground water supplies or other
pollution or nuisance.

3.23  Drainage of Surface Water.  The entire site, including the fill surface, shall be graded and/or
provided with drainage facilities to minimize run-off into and onto the fill, prevent erosion or
washing of  the fill, drain off rain or other precfpitation falling on the  fill, and to prevent the
collection of standing water.  The final surface of the fill shall be graded to slope at least 1%,
but no slope shall be so steep as  to cause erosion of the cover.

3.24  Animal Feeding.  All animals shall be excluded from the site.

3.25  Salvage. No salvaging or scavenging shall be permitted at the site.

3.26  Safety. Site personnel shall be instructed in the principals of first aid and safety and  in the
specific operational procedures necessary to prevent accidents.  Accident precautionary measures
shall be employed at the  site.  An adequate stock of first aid supplies shall be maintained at the
site.

3.27  Communications. Telephone or radio communication shall be provided at or near the sanitary
landfill site.

3.28  Initial  Development of Site.  Prior to filling any waste, the initial development of the site
must have been completed.  Initial development shall include the following:  roads, grading,  '
                                           IV-13

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 Document  IV-2,  Page 4


drainage, utilities, structures, fencing,  berms,  sight screening and litter control fencing.  During
the first planting season initial landscaping and  ground cover shall be established.

3.29 Operational Plan. Prior to filling any waste,  an operational plan must be prepared.  This
plan shall show the intended filling of the site and shall include layout and elevation of lifts,
sequences, sources and quantities of cover material, drainage, temporary roads and final develop-
ment of the site.

3.30 Operational Records and Plan  Execution.  A daily log shall be maintained showing location,
type and quantity of material being placed in the  fill.  A copy of the plan,  specifications, instruc-
tions and other documents showing how the filling is to be  carried out shall be maintained at the
site.  Lines,  grades, and other control devices shall be placed in  the fill area prior to filling and
shall be maintained as required to provide a visual reference for equipment operators.

SECTION 4.  Any person may establish and operate  a private sanitary landfill for the disposal of
his own solid wastes  provided he shall  have first applied for and received a permit from the city
designating his site a "Licensed Private Sanitary Landfill"  and may continue to do so as  long as the
permit shall remain in  force and the  site is operated  in accordance with the provisions of this ordi-
nance.

Licensed Private  Sanitary Landfill sites shall be  used for the exclusive purpose of disposing  of the
site operator's own waste and shall not be open to any segment of the general public nor to any
other private source  of waste .

It shall be  unlawful for any person to receive  payment of any kind, or request  payment of any kind,
for the disposal of any garbage or refuse at a private licensed sanitary landfill site.  The charging
of a  fee for the collection  and disposal of any garbage or refuse from a customer by  a private refuse
collector shall not be construed as a violation of this Section since the disposal is considered to be
incidental  to the total collection and disposal service, provided however, such collection and
disposal shall be  conducted entirely  by forces and with equipment owned or operated by the private
refuse collector.

The issue of this permit shall be in the manner prescribed by the City and subject to all other appli-
cable Ordinances of the City. Application permits shall include all  necessary data to show that
the landfill will be operated in accordance with the Sanitary Landfill Standards included in Sec-
tion  3.  Included in  part must be:  a topographic map of the existing  land; preliminary plans of the
initial  development; preliminary operation plans; sources of cover material; equipment proposed
for use and other data  as may be required. Also included shall be.an agreement by  the applicant
to maintain his landfill site and the vicinity in a safe and sanitary manner, to  allow no public
nuisance, and to provide a responsible person who will be  in constant attendance during the hours
of active operation;  agreement to operate his  landfill in accordance with all local, county, state
and federal regulations and to permit access to the landfill site by any health officer or  govern-
mental representative or agent who may  have  jurisdiction for the purposes of inspection.

An annual  license fee  of $300.00 per year shall  be paid to the City for each location at which a
landfill is conducted.

If any private landfill  operation is found to be conducted in a way detrimental to the health and
welfare of the public,  or contrary to provisions of this ordinance, the Health Officer shall  notify
the operator in writing of the objectionable conditions and give him a reasonable time to correct
said  conditions.  After proper notice, the City is authorized to enter upon the premises and use
any of the  City's forces and equipment, or those of the landfill operator, or hire forces and equip-
ment to correct the objectionable conditions.  The same shall be considered of benefit to the Owner
of the land and the cost of such corrective action  shall be  chargeable to the Owner, and if not paid,
shall constitute a lien  upon the premises and shall  be collected in the same manner as taxes as pro-
vided by law.

SECTION 5.  Any person may establish and operate  a private landfill for the disposal of "Construc-
tion  Demolition Waste" originating from  the operator's own demolition work, provided he shall
have first applied for and received a permit from the City designating his site a "Licensed Private
Landfill, "  and may do so as long as the permit shall  remain in force and the site is operated in
accordance with  the provisions of this Ordinance.
                                             IV-14

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Document IV-2, Page 5


Licensed Private Landfill sites shall be used for the exclusive purpose of disposing of the site
operator's own waste and shall not be open to any segment of the general  public nor to any other
private source of waste.

It shall be unlawful for any person to receive payment of any kind or request payment  of any kind
for the disposal of any construction demolition waste at a  Private Landfill site.  The charging of
a fee for demolition and disposal of a structure or pavement or other physical facility shall not be
considered as a violation of this section since the disposal  is considered to be incidental to such
demolition and disposal service provided demolition and disposal shall be conducted entirely by
forces and with equipment  owned or operated by  the site operator.

The issuance of this permit shall be in a manner prescribed by the City and subject to all other
applicable Ordinances of the City.

Applications for permits shall include all necessary data to show that the  landfill will  be operated
in accordance with the Sanitary Landfill Standandards included  in Section 3 except the provision
for On-Site  Roads, Quantity Measurements,  Unloading, Daily  & Intermediate Cover,  Special
Materials, Animal Feeding, and Operation Records and Plan Execution shall not be required.

In  lieu of the daily and Intermediate Cover requirements as written, the operator shall be required
to comply with this standard only for that part of the material which is combustible or  which is
subject to being scattered by the wind causing wind blown litter.

Included in  part must  be:  a topographic map of the existing land; preliminary plan for the initial
development; preliminary operation plans;  sources of cover material; equipment proposed for use
and other data as may be required.  Also included shall be an agreement  by the applicant to main-
tain  his landfill site and the vicinity in a safe and sanitary manner,  to allow no public nuisance, and
to provide a responsible person who will be in constant attendance during the hours of active opera-
tion; agreement to operate his landfill in accordance with all local, county, state and federal regu-
lations and to permit access to the landfill site by any health officer or governmental representative
or agent  who may  have jurisdiction for the purposes of inspection.

An annual license fee of $300.00 per year shall be paid to the  City  for each location  at which a
landfill is conducted.

If any private landfill operation is found to be conducted  in a way detrimental to  the health and
welfare of the public, or contrary to provisions of this ordinance, the Health Officer shall notify
the operator in writing of the objectionable conditions  and give him a reasonable  time to correct
said conditions.  After proper notice, the City is authorized to enter upon the premises and use
any of the City's forces and equipment, or those  of the landfill operator,  or hire forces and equip-
ment, to correct the objectionable conditions. The same  shall  be considered of benefit to the Owner
of the land and the cost of such corrective action shall be  chargeable to the Owner, and if not paid,
shall constitute a lien upon the premises and shall be collected in the same manner as  taxes as pro-
vided by law.

SECTION 6.  No  person shall dispose of garbage or refuse of any kind upon any land within the
jurisdiction  of the City, except as provided in Section  5, unless such land has been designated
by the City  as a "Licensed Private Sanitary Landfill" or a  "Public Sanitary Landfill" and then only
in compliance with posted  or published instructions or at the direction of  an attendant in charge.

SECTION 7.  Nothing in this ordinance shall apply to  the filling, leveling or grading of land with
earth, sand, ashes, cinders, slag, gravel, rock,  or similar inert wastes, provided these materials
are not contaminated  or mixed with other waste materials;  nor to the disposal of animal and agri-
cultural wastes on farm land.

SECTION 8.  It shall be unlawful for any person, firm  or  corporation to sell or offer for sale, or to
install or offer to install, any device intended for use  as a garbage or refuse burner or incinerator;
except when the intended user of such a device has secured a license to operate such a device from
the City, or when the device will be operated by or for the City.

SECTION 9.  It shall be unlawful for any person  to burn or incinerate or  permit the burning or in-
cineration of any garbage or refuse within the jurisdiction  of the City. This section shall apply to
                                         IV-15

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Document IV-2, Fbge 6


all garbage and refuse as defined,  and shall specifically include all waste paper, boxes, market
waste, garden wastes,  trees, tree limbs,  leaves and any and all materials other than materials used
as a fuel in a furnace or boiler.

This section shall not apply to  any  incinerator operated under a license granted by the City or any
incinerator operated by or for the City, or any burning conducted under the direction of the Fire
Department of the City.

SECTION 10.  It shall be the duty of the Health Officer and all police officers of the City to en-
force  the provisions of this ordinance.

SECTION 11  .  Ordinance No.       and all ordinances or parts of ordinances  in conflict with this
ordinance are hereby  repealed.

SECTION 12.  If any section, subsection,  sentence or part of this ordinance is for any reason held
to be  invalid or unconstitutional, such decision shall not affect the validity of  the remaining por-
tions  of this ordinance.

SECTION 13.  Any person violating any of the provisions of this ordinance shall upon conviction
be subject to a fine of not more than $100.00 or to imprisonment for not more than 30 days.

SECTION 14.  This Ordinance shall be in full force and  effect from and after its passage and
publication as provided by low.


PASSED AND AFP ROVED this	day  of	, 19	
                                                      Mayor

Attest:


          City Clerk
                                         IV-16

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 DOCUMENT IV-3, fbge 1

 PROPOSED REFUSE COLLECTION ORDINANCE FOR CITIES, TOWNS AND VILLAGES CONTRACT-
ING WITH THE OMAHA-COUNCIL BLUFFS METROPOLITAN SOLID WASTE AGENCY

                                 Ordinance No.
AN ORDINANCE PROVIDING FOR MUNICIPAL COLLECTION OF GARBAGE  AND REFUSE;
DEFINING TERMS:  PRESCRIBING  RULES AND REGULATIONS THEREFOR;  REGULATING THE
PRIVATE COLLECTION OF GARBAGE AND REFUSE; PROVIDING FOR THE LICENSING AND
REGULATION OF PRIVATE GARBAGE AND REFUSE COLLECTORS; PRESCRIBING RULES AND
REGULATIONS FOR HAULSNG GARBAGE,  REFUSE AND OTHER WASTE MATERIALS WITHIN OR
THROUGH THE CITY; PROHIBITING THE DEPOSIT OF LITTER WITHIN THE CITY; PROVIDING
PENALTIES FOR VIOLATION THEREOF;  AND REPEALING ORDINANCE NO.	
AND ALL OTHER ORDINANCES AND PARTS OF ORDINANCES IN CONFLICT THEREWITH.

BE IT ORDAINED BY THE CITY COUNCIL OF THE CITY OF
SECTION 1:  For the purpose of this Ordinance the following definitions shall  apply:

1.1  "Agency" shall mean the Omaha-Council Bluffs Metropolitan Area Solid Waste Agency.

1.2  "Person" shall mean any individual,  firm, association, syndicate, co-partnership, corporation,
trust, other legal entity having proprietary interest  in a premise,  or other legal entity having
responsibility for an act.

1.3  "Garbage" shall mean the solid or semi-solid animal and vegetable waste resulting from the
handling, preparation, cooling and serving of foods, including cans, bottles and cartons in which
it was received and wrappings in which it may be placed for disposal.

1.4  "Refuse" shall mean all solid waste from residential, commercial or industrial premises.  It
shall include semi-liquid or wet wastes with insufficient moisture  and other liquid contents to be
free  flowing.   It shall not include any construction materials except minor amounts  incidental
to other wastes.

1.5  "Health Office" shall mean (each city,  Town, Village and County should indicate who shall
be the Health Officer, who shall have  responsibility for administering and enforcing this ordinance.)

SECTION 2:  By virtue of an agreement dated	 between the City and the Agency,
the Agency has agreed to provide garbage and refuse collection and disposal service for and on
behalf of the City, to remove all garbage and refuse from (specify who  is to receive service;
i.e., dwellings,  commercial, etc.) located within the City, subject to the following conditions:

2.1  Collections shall be made not less than (specify number of times per week) a week, at such
time  and in such areas of the City as shall be set out in schedules agreed upon by the City and the
Agency.

2.2  The City and the Agency are authorized and empowered, jointly,  to change or amend such
schedules from time to time as they, in their discretion, shall  deem necessary.

2.3  Collections may be made either from streets or alleys, where existing, at the discretion of
the Agency personnel.

2.4  Containers shall be placed out-of-doors at some easily accessible  place.

2.5  (Specify other conditions as necessary.)

SECTION 3.  Refuse containers and garbage containers shall not be more than 30 gallons nor less
than  10 gallons in nominal capacity; except where only one container is used,  in which case this
containers may be  less than 10 gallons in capacity.  Containers shall be waterproof, rat proof,
and fitted with a  tight lid.  The containers shall have handles, bails  or other suitable lifting devices
                                        IV-17

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Document IV-3, Page 2


or features.  The containers shall be of a type originally manufactured for refuse or garbage, with
tapered sides for easy emptying.  They shall be of light weight and sturdy construction.  The
weight of any individual container and contents shall not exceed 65 pounds.  Galvanized iron and
similar metal containers, rubber or fiberglass containers, and plastic containers which do not become
brittle in cold weather may be used.  Disposable bags manufactuied for garbage and refuse disposal
in suitable frames or containers shall be acceptable.  Oil or grease drums, paint cans, and similar
salvaged containers shall not be acceptable.

3.1  All refuse and garbage shall be placed in suitable  containers; except,  it shall not be necessary
to place books, boxes, magazines, or newspapers in containers provided they are securely tied in
bundles or completely contained in disposable boxes not larger than 24 x 24 x 36 inches.  Also
tree limbs and brush may be securely tied in bundles not larger than 48 inches long and 18 inches
in diameter.
3.2  Baskets, boxes and non-complying refuse or garbage cans or containers shall  be considered
disposable refuse and shall be removed by the Agency collection crews if they are the proper size
and otherwise acceptable for collection;  or shall be left uncollecred if they are  larger than the
allowable size or unacceptable for collection.

3.3  Large bulky  items such as furniture, large tree  limbs and appliances that cannot be reduced
to fit approved containers, will  not be collected. (City to specify alternate collection if
desired.)

SECTION 4.  Within the corporate limits of the City, all garbage or refuse, consisting of waste
animal and vegetable matter, which may attract flies,  dogs or rodents, shall be drained of all
excess liquid, wrapped in paper or disposable containers, and placed or stored, until collected,
in covered suitable containers as described  in Section 3.

SECTION 5.  It shall be unlawful for any person to  permit to  accumulate on any premises, improved
or vacant,  or on any public place in the City, such quantities of garbage or refuse, either in
containers or not,  that shall,  in the opinion of the Health Officer, constitute a health or sanitation
hazard.
 SECTION 6.  It shall be unlawful for any person to permit to accumulate quantities of refuse,
 papers, trash, ashes, or other waste materials, within or close to any building in the City, unless
 the same is stored in containers in such a manner as not to create a health or fire hazard.

 SECTION 7.  No person shall engage in the business  of removing or hauling garbage or refuse from
 the premises of others unless such person shall have first applied for and received a permit to  do so
 from the City. Application  for such permit shall specify the equipment or vehicles to be used,
 general information concerning the  route to be traveled and the places to be served, and the name
 and address of the applicant.  Such person shall pay  an annual license  fee of Fifty Dollars (50.00)
 per year for each vehicle engaged  in such business to be paid at the office of the City Clerk.
 Such permit fee shall be payable commencing on the	day  of
 19    , and shall be renewable each year thereafter"All vehicles licensed under this section shall
 prominently display the  license number on the left and right sides of the vehicle in letters not less
 than 3" high.

 SECTION 8.   Any person authorized and licensed by the Agency to remove or haul, garbage or
 refuse, shall be considered to have met the provisions of Section 7, and no further permit or license
 shall be required by the City.

 SECTION 9.  No person shall haul any garbage or refuse upon the streets, alleys or public places
 of the City, unless the same shall be in approved containers, securely fastened to prevent spillage,
 or in a totally enclosed water tight vehicle.  If, however, the material is a dry  type material, it
 may be hauled in a totally enclosed vehicle, or open vehicle which is covered with a suitable
 tight fitting canvas tarpaulin or similar cover to prevent spillage.  Licensed collectors who collect
 and haul  garbage and/or refuse shall haul these materials only in totally enclosed vehicles with
 water tight containers.  All vehicles used for rhe collection and removal of garbage and refuse
 shall be kept in a clean, inoffensive and sanitary condition. All garbage and refuse shall be
 handled in such a way as to prevent  the scattering,  spilling or leakage of same.
                                         IV-18

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 Document IV-3, Page 3


SECTION  10.  No person shall  haul or cause to be hauled any garbage,  refuse or other waste
material of any kind, to any dumping place or site or area, within or without the corporate limits
of the City, unless such place,  site or area is first licensed by the City,  or is an Agency operated
sanitary landfill site; in addition to complying with all applicable health and zoning ordinances of
the City.

SECTION  11.  No person shall  deposit in a garbage  or refuse container or otherwise offer for
Agency collection any  hazardous garbage, refuse, or waste.  Hazardous materials shall be trans-
ported by the owner, responsible person or his agent, to a place  of safe deposit or disposal as
prescribed by the Health Officer or his authorized representative.  Hazardous  materials shall
include:  Explosive materials; rags  or other waste  soaked in volatile and inflammable materials;
drugs; poisons;  radio active materials, highly combustible materials; soiled dressings, clothing,
bedding and/or other wastes,  contaminated by infection or contagious disease,  and  other materials
which may present a special hazard to collection  or disposal personnel  or equipment or to the public.

SECTION  12.  No person shall  throw, rake, deposit, dump, drop or spill litter, waste material
or foreign material  upon the streets, sidewalks,  or other public rights-of-way within the City.
However, the Mayor may at his discretion proclaim a period when  leaves may be placed in street
right-of-ways for collection.

SECTION  13.   It shall be the duty  of the Health Officer and all  police officers of the City to
enforce the provision of this ordinance.

SECTION 14.   Ordinance  No.              and  all  ordinances or parts of ordinances in conflict
with this ordinance are  hereby repealed.

SECTION  15.   If any section, subsection,  sentence or part of this  ordinance is for any reason held
to be invalid or unconstitutional, such decision shall  not affect the validity of the remaining
portions of this ordinance.

SECTION 16.   Any person, firm or corporation violating any of the provisions  of this ordinance
shall  upon conviction be subject to a fine of not more than $100.00 or  to imprisonment for not more
than 30 days.

SECTION 17.   This Ordinance  shall  be  in full force and effect from and after its passage and
publication as provided by law.


PASSED AND APPROVED this	day of  	, 19	.
                                                                 Mayor


Attest:



         City Clerk
                                            IV-19

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required annual operating revenue and debt service on the bonds can be raised
from fees charged by the Agency for disposal services  rendered to the member
comrn unities.

The details  of the financing should be worked out by financial consultants at
the proper time. In this section,  the revenue requirements and the fees
necessary to meet these requirements are summarized.

Bond authorities informally doubt that the Agency,  created under the provisions
of Chapter 28E, Code  of Iowa and provisions of Chapter 23, Article 22 of the
Statutes of Nebraska would have the  specific  authority to issue bonds of any
kind.   Apparently this matter has not been necessary to date nor tested in any
court.  It would be  beneficial if this  authority were added to the  provisions of
the two state laws.   Without such specific  authority, potential bond buyers
would be reluctant to purchase the bonds.  As an alternative it has been
suggested that  a declaratory judgment be  requested from appropriate courts,
stating that the  authority to issue  bonds is implied in the language of the  laws
and that an Agency  so  organized has such authority.  The decision on this
matter should be made by competent legal counsel.  In any case, specific
legislation should be requested granting this  authority to the Agency.

In the event the Agency cannot issue revenue bonds in the name of the Agency,
it is recommended  that one of the member municipalities issue the  bonds under
its own authority.  The capital investments made with the  bond proceeds would
be held in the name of the municipality, at least until the bonds were paid.
Meanwhile,  land, improvements and equipment purchased with the bond pro-
ceeds would be  leased to the Agency.  The lease  agreement and a pledge of
the required funds from fees would be used as security to  back the revenue
bonds.

Revenue  bonds do not affect the general bonding power of the municipality.
They are not included  in statutory debt limits nor are they an obligation of the
municipality.   Revenue bonds are  secured only by the revenue produced by the
activity for  which they were  issued.

We suggest  that the City of Omaha should be  the municipality to issue the
revenue bonds  for the  needed capital associated with  the four sites in the urban
area.  Sites 3 and 7 are within Omaha's political jurisdiction.   Sites 1 and 5
are within the political jurisdiction of Sarpy County and Council Bluffs res-
pectively.  Omaha should enter into specific  contractual agreements with
these two jurisdictions to maintain proper access to these sites and assure
their continued  use.  Omaha has need for these four sites  and  has the authority
to issue revenue bonds.   It is also in the interest of Omaha to  provide facilities
in excess of their own needs, to obtain a larger operation, and thus a more
economical  operation, resulting in a lower unit cost.  The sites recommended
are placed in such a position to be used economically by waste  producers other
than Omaha.
                                    IV-20

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Wt: suggest one of the cities in eastern Pottawattamie County issue the
necessary  revenue bonds to finance Site No. 8.

               b.    Operating Revenue.  Operating revenue and debt service
for bonds can be obtained from fees charged to the users of the sites.  Initial
operating funds may be  obtained from assessments to the member municipalities
dnd.from the pre-sale of disposal fee coupons or tickets.

               j;.    Revenue Required.  The amount of revenue required for
annual operating expense and debt service is summarized in Table IV-1.  The
cost estimates from which this table was prepared are explained  in Part III.
D.4.  of this report.

The bond issue requirements for the  anticipated one  time capital  investment
are as follows:

               Urban Sites 1,  3,  5 & 7   $ Z, 034, 000
               Rural Site 8              	83,000
                              Total       $ 2, 117,000

The total revenue  requirement,  including debt service,  debt service reserve
and annual expenses is estimated to be $949, 100 per year for the first year
(1970).

                            TABLE IV-1

             REVENUE REQUIREMENT AND INCOME FOR
                 AGENCY DISPOSAL OF SOLID WASTE

        A.    REVENUE REQUIREMENTS

               1 .    First Year, 1970

                    _a.    Fixed Cost                 $408,800
                     b.    Variable Cost                466,500
                    _£.    Debt Service Reserve          73, 800

                          Total Revenue Required     $ 949, 100

               2.    Fourth Year,  1973

                    _a.    Fixed Cost                 $408,800
                    _b.    Variable Cost                429,200
                    _c.    Debt Service Reserve	73, 800

                          Total Revenue Required     $ 911,800

        B.     INCOME
               1.    First Year, 1970
                       751,200 Tons @ $1.40/Ton =  $1, 051, 700
               2.    Fourth Year,  1973
                       691, 000 Tons @ $1.40/Ton -  $  967,400
                                  IV-21

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                Q-     Income: .  It will be necessary to provide income which
is equal to the  required revenue shown in Table IV-1.  This income will be
provided from  fees charged to the users of the facilities.  The expected in-
come is shown in Table IV-1.

                e_.     Disposal Fees .  The disposal operation should be
i omplc-tely self-supporting by charging  fees from the users of the facilities.
Several systems for charging of fees are possible and are explained in the
Appendix in Exhibit IV-1.   The recommended system is based on the weight
of material brought to the site in each vehicle.  This requires scales and
scale operators which are included  in the estimates for Sites 3, 5 and 7.  In
the case of the Rural Site No.  8,  such a small operation could not justify  the
expense of the  use  of truck scales.  Therefore we recommend a fee based on
volume of refuse be used which would be equivalent to the fee  per ton charged
at the other sites.  Also, in the early years of operation of Urban Site No.  1,
there would be insufficient waste  to justify scales. We recommend  a volu-
metric fee system  for this  site for the first several years. .

The proposed fees  are developed and explained in Part III.D.7.  of this report.

        2.      Collection System.   The scope of this report does not include
collection of  solid waste; however we have briefly discussed in Part III of
this report, the collection of certain solid wastes in the rural communities
of eastern Pottawattarnie County.  We have also included collection  of solid
waste in the purpose and powers  of the Agency.   If the Agency would elect
to provide collection service at this time the capital cost and operating ex-
pense could be billed to those communities being served.

We recommend that collection service and disposal service be treated as two
separate and distinct operations and that separate accounting be provided for
the necessary funds.
                                 IV-22

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_H.	INTERIM ACTIVITIES.  While the Agency is being formed an interim
director should be appointed to guide the formation of the Agency, the prelim-
inary work on financing and legislative problems, and the selection and hiring
of«a qualified permanent director.  It would be desirable if the permanent
director could be hired and the Agency brought into being within a few months.

The Agency has many activities which must be accomplished prior to starting
collection or  disposal of solid waste.  Once the  director is hired the following
items  should  be accomplished;

         1.     Review the report recommendations  and prepare a detailed
statement of policy.  There  are several recommendations which the member
municipalities may wish to modify and several which are stated in general
terms, which must be defined in light  of the particular needs of the members.

         2.     Review the report and make adjustments where necessary
after it has been determined which municipalities have agreed to join the
Agency.

         3.     With the aid of fiscal and legal consultants prepare the financ-
ing and legislative procedures, and pursue these matters at the proper time.

         4.     Conduct sanitary landfill site  investigations and  select the
specific parcels of land to purchase.

         5.     Design the initial development of the  sites which  have been
selected.

         6.      Assist the member municipalities in  the interim  improvements
to their disposal facilities and the necessary arrangements to close the sites
which are  not to be continued.

         7.      Determine the total equipment needs  of the Agency as formed.
Those  needs will include leased equipment from those members with  surplus
equipment and. new equipment.  Prepare cost estimates for the purchase of
equipment not being leased and cost estimates and schedules for initial purchase
of equipment as leased equipment is  replaced with Agency owned  equipment.

        8.      Plan for the staffing of the Agency with regard for the employees
now working in collection and disposal divisions in the member communities,
and the recruitment and hiring of new personnel.

        9.      Prepare standard operating procedures, job descriptions,
operating instructions and policies of the Agency which are pertinent to the
operation of the collection and disposal services.

         10.     Plan the now collection routes which  may be required to m«:et
the needs  of requested collection service,  if the Agency decides to provide such
service.

                                    IV-23

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         11.     Determine the new revenue requirements and projected income
based on actual conditions which will prevail at the time of operation.

         IZ.     Prepare all of the details for the orderly commencement of
operation.

         1'i.     Assist in the sale of revenue bonds to produce the necessary    '
initial capital.

         14.     Purchase  the land and equipment, construct the necessary
improvements,  acquire the personnel.

         15.     Place the  Agency into operation.

Part of the interim activities will require the assistance of specialists and
consultants.  Where there are member municipalities which have the required
specialists on their staff and their duties will permit, these  staff members may
be used to advantage.   It will probably be necessary to hire bond consultants
in connection with the issuance of revenue bonds and  engineering consultants
to assist in the details of site selection and initial site development.

To finance the interim activities, it is recommended that an initial budget
based upon per capita membership be paid to the Agency by the joining members.

This budget should include funds for the support of the director and his staff,
required consultants  and the initial operating funds for disposal facilities.

I         STATE LEGISLATION
         1.      Financing and Eminent Domain.   The State Legislation upon
which the recommended Agency would be formed is described in Section C of
this Part IV of the  report.  There are two areas  in which the existing legislation
is inadequate, i. e.  ; there is no specific provision for the Agency to issue the
required revenue bonds for the long-term capital financing and there is no
specific provision for the agency to exercise the  right of eminent domain.

To overcome the first deficiency, we have  recommended in Section G, Part IV
that the necessary  revenue bonds be issued by a member municipality.  To
overcome the second defiency, the exercise of eminent domain,  if condemnation
became necessary,  could be accomplished by the member municipality in
whose jurisdiction  the site was located.

It would be helpful  if revenue financing and eminent domain authority were
specifically provided in the laws of  both Nebraska and Iowa.

In a solid waste report prepared for the metropolitan area of Des Moines  in
1968, we recommended a similar agency be created under the provisions  of
Chapter 28E of the  Iowa Code.  We  also recommended that the new agency


                                   IV-24

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 pursue the problems of revenue bond financing and eminent domain with the
 State legislature.  At the time  of the final writing of this report,  the Iowa
 Legislature has  passed the required legislation.   The language of the act can
 be found in Senate File 482.  We recommend legislation be passed in the State
 of Nebraska which would have the same effect as that found in the language of
 the Iowa bill.

         2.       Authority of the Various  Subdivisions of the State  In various
 places in the  statutes of Iowa and Nebraska, authority has been given to cities
 of the several classes,  towns,  villages and counties,  to provide for the collec-
 tion or disposal  of solid waste  or both.  In some cases this was accomplished by
 adding solid waste or words meaning solid waste to a list of other subjects
 covered; and  in others,  authority was specifically designated for  solid waste
 matters.  Some  provisions specifically state "removal or disposal  of garbage"
 whereas in other cases  "disposal" is stated and it is presumed that "removal"
 is implied.  In some cases there are controls on taxes and requirements for
 referendums  and in others  there are not.

 As a practical matter, most  communities can probably find adequate  authority
 either expressed or implied to  provide some form of collection and disposal
 of solid waste.  It would be helpful,  however, if adequate state laws concerning
 solid waste matters were available that granted broad specific powers to all
 cities, towns, villages and counties.  This is particularly true when several
 political subdivisions of various classes join together to solve solid waste
 problems through an area wide  agency approach such as is contemplated in
 this report because the Agency cannot do  anything for a member municipality
which the member does  not have the authority to do for itself.

We have prepared a Proposed Solid Waste Disposal Act in the  form of a bill
which brings together under one title the authority for all cities,  towns,
villages and counties to  handle  solid waste problems.  This proposed bill is
enclosed in this Part IV of the report as Document IV-4.  This bill  contains
provisions that we  believe to  be necessary and desirable from a viewpoint
of public works,  sanitation and  solid waste management.  It should  be
reviewed by competent legal counsel for matters of law and individual state
constitution requirements.

As an alternate to this proposed act, we would recommend the various statutes
of Iowa and Nebraska concerning solid waste matters be compared to  the
provisions in  thia act and the existing statutes be revised where necessary
and desirable.

As a further alternate and as a  minimum, we would recommend the following
specific revisions:

                a.      Collection of Garbage and  Refuse in Iowa  Cities and
Towns ,  In Section 368. 24 - Garbage and  Refuse Disposal of the Iowa Code,
the power to establish a schedule of fees for garbage collection and certain

                                  IV-2 5

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DOCUMENT IV-4,  Page 1   PROPOSED SOLID WASTE DISPOSAL ACT

A BILL FOR AN ACT

RELATING TO SOLID WASTE DISPOSAL POWERS AND DUTIES, FINANCING THEREFOR:
FIXING  RATES AND CHARGES,  COLLECTION THEREOF; CONTRACTING WITH PRIVATE
PARTIES; SETTING MINIMUM STANDARDS, VIOLATIONS AND PENALTIES  THEREFOR.

BE IT ENACTED BY THE LEGISLATURE OF THE STATE OF (IOWA) (NEBRASKA):

SECTION 1.  DEFINITIONS.   Subdivision  1 .  As used in Section 1 to 15, the terms defined in
this section  have the meaning given them, except as otherwise provided or indicated by the context.

Subd. 2.  "Solid Waste."  "Waste" is  unwanted or discarded material resulting from commercial,
industrial and  agricultural operations and normal community activities. Waste  include solids,
liquids and gases.  Wastes which are solid or semi-solid containing insufficient liquid to be free
flowing are  classed as solid waste.  Solid Waste is  refuse and  includes in part the following:
garbage; rubbish; ashes and other  residue after burning; street refuse; dead animals,  animal waste;
abandoned vehicles; agricultural, commercial and  industrial waste; construction and demolition
waste; and sewage treatment residue.

Subd. 3.  "Solid Waste Disposal" means the storage, removal and collection of solid waste from
public and  private property, and its transportation  to disposal facilities and its ultimate disposal
by landfill,  sanitary  landfill, composting, incineration or other authorized and approved  methods.

Subd. 4.  "Facilities" means all or any vehicles, mechanical apparatus,  equipment, machinery,
incinerators, plants,  buildings, structures, shop or office space,  furniture  and  equipment, public
or private grounds, purchased, leased, erected, constructed,  or otherwise permanently or
temporarily  acquired, for the storage removal, collection,  transportation  and disposal of solid
wastes.

Subd. 5.  "Sanitary  Landfill" is a controlled method of disposing of refuse on land without creating
air,  land or water pollution or nuisances or hazards to public  health, welfare or safety, by
utilizing the principles of engineering  to confine the refuse to the smallest practical volume,  and
to cover  it with a  layer of earth at the conclusion of each  day's operation, or at such more
frequent  intervals as  may be necessary.

Subd. 6.  "Landfill" is the same as a sanitary landfill, except cover material is applied from time
to time as required, instead of daily or more frequently.  To be acceptable,  landfills must be
restricted to inert, non-combustible, non-putrescible solid waste materials.

Subd. 7.   "Incineration" is the controlled process  of burning  solid,  semi-solid, liquid or  gaseous
combustible wastes in an enclosed device, producing an  inoffensive gas and a sterile residue
containing  little or no combustible material.  The process is used to reduce the volume
of waste  material or to change the characteristics of hazardous wastes to a safer form.

Subd. 8.  "Pollution"  is the contamination of any  air, water,  or land so as to  create a nuisance
or render such air, water or land unclean or noxious, or impure so as to be actually or potentially
harmful or detrimental or injurious to public health, safety or welfare, to domestic, commercial,
industrial or recreational use,  or to livestock, wild animals, birds, fish, or other aquatic  life
or to plant  life.

Subd.  9.   "Municipality" for the purpose of sections 1 to  15  means a city of any class, town,
village,  or a county  representing  its unorganized territory, town  or other  governmental subdivision,
however  organized.

Subd.  10.   "Governing Body" means the board, council, trustees, commission, or other body of the
municipality charged with the general  control of its financial affairs; provided, that where the
charter or law under which a  municipality is organized confers bond issuing power or contracting
authority on a particular boarder  body, such board or body is the governing  body  under the
provisions of sections 1 to 15.
                                            IV-26

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Document IV-4, Page 2


SECTION 2.  DISPOSAL FACILITIES; AUTHORITY.   Any municipality is hereby authorized and
empowered to collect and remove solid waste from public  and  private property,  and to transport
and dispose  of solid waste, and for these purposes is authorized and empowered (1) to acquire
by gift, lease, purchase, or condemnation as provided by law, any land or interest in land, within
or outside of the municipality,  on which the governing body deems suitable to establish or operate
facilities for the collection, transportation and disposal of solid wastes;  (2) to purchase,  lease,
establish, erect, or construct facilities on such site or sites; (3) to enlarge, improve,  repair,
supervise, control, maintain and operate such facilities for disposal of solid waste;  (4) to purchase
or lease materials, equipment and machinery necessary in connection with the operation and
maintenance of facilities for removal, collection,  transportation and  disposal of solid wastes;
(5) to employ such personnel as may be necessary for the care, maintenance and operation of such
facilities.

SECTION 3.  BONDS AND TAXATION.

Subd.  1 .  The governing body of a municipality, however organized, is hereby authorized and
empowered for the purpose  designated in Section 2 of this Act, or  for refunding  bonds, to issue,
from time to time as needed,  the negotiable bonds of  the municipality to the amount authorized
by the governing body.

Subd. 2.  The bonds shall be issued, negotiated, and sold in the manner and subject to the  conditions
prescribed by the	(list the  appropriate statute provision or recite new provision as required)-  -
—	, as heretofore or hereafter amended, so far as applicable to the municipality issuing bonds,
except as herein otherwise  expressly provided,  and may levy all taxes necessary therefore.  Such
bonds and interest thereon and the expense of issuance thereof may be paid out of the proceeds of
tax levies or out of revenue from fees or other sources, or both, and the governing body may pledge
any such proceeds or revenues thereto.

Subd. 3.

(1) Nothing herein contained shall preclude a  municipality from issuing revenue bonds for the pur-
poses set forth under Section 2 of this Act, or to refund  bonds.  Such  revenue bonds shall not impose
any general  liability upon the municipality but shall be secured only  out of revenues derived from
the charges as provided in Section 4.  Such charges for  solid waste disposal service shall be suf-
ficient, at all times, to pay the cost of operation and mai ntenance thereof and to pay the principal
of and the interest upon all revenue bonds issued,  and to carry out all covenants that may be provided
in the ordinance authorizing the issuance of any such  bonds.
(2) Revenue bonds shall be issued, negotiated and sold  in the manner and subject to the conditions
prescribed by the	(list the appropriate statute provisions or recite new provisions as
required)—  , as heretofore or hereafter amended,  so far as applicable to the municipality issuing
the bonds, except as herein otherwise expressly provided.

Subd. 4.
(1)  The governing body of any municipality may  levy taxes for any solid waste disposal purpose on
all property taxable within the municipality.  Any taxes, levied or to be  levied, and any bonds or
other evidences of indebtedness Issued or to be issued for the purposes designated in Section 2 of
this act, or any part thereof, shall not be subject to any limitation of a charter or state law and shall
be excluded in computing amounts subject to any limitation on tax levies, bonded indebtedness or
other indebtedness and the governing or managing body and the  proper officers of the municipality
concerned  shall have the power and  it shall be their duty to levy such taxes and issue such bonds
and take such other lawful actions as may be appropriate and necessary  to provide funds to meet the
cost  of accomplishing such purposes, notwithstanding any such limit and without any election or
referendum therefor.
(2)  A recital  in any bond, or tax levy, that the same is issued or made  for the purposes of a  solid
waste disposal facility or facilities,  or any part thereof, is not subject to  any  provisions of law pre-
scribing limits or  requiring an election or referendum therefore,  and shall  be prima facie evidence
thereof and that all requirements of  law relating thereto have been complied with. In any suit,
action, or  proceedings involving the validity or enforceability of any bonds of a municipality or  the
security therefor, any such bond reciting in substance that  it has been issued by the municipality to
aid in financing a solid waste disposal facility  or facilities, or any part thereof, shall be conclusively
deemed to  have been issued for such purpose, and in compliance with all  requirements of the  law
relating thereto.
                                           IV-27

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 Document IV-4, Page 3


(3)  For any solid waste disposal purpose, a municipality may levy taxes in anticipation of need and
the provisions of this subdivision shall be applicable so far as appropriate to any such anticipatory
levy.  If such a tax is levied in anticipation of need,  the  purpose must be specified in the resolution
of the governing body directing the levy, and proceeds of the tax must be used only for that purpose,
and until used the proceeds shall be retained  in a separate fund, or  invested, as surplus in a sinking
fund may be invested under - — (list appropriate statute provisions or recite new provisions as
required)	.

Subd. 5.   In exercising power and authority under Sections 1 to 15, the action of the governing
body of any municipality shall not be subject to approval of a board of estimate and taxation,  nor
subject  to the provisions of a charter prescribing a particular method of authorizing issuance of bonds.

SECTION 4. EQUITABLE CHARGES FOR SOLID WASTE DISPOSAL SERVICES .  Any municipality
which has established and is operating, or which is proceeding to establish, or which may hereafter
establish facilities for, or contracts for removal, collection, transporation or disposal  of solid waste,
in addition to all other powers granted to it,  shall have authority, by  an ordinance duly adopted by
the governing body thereof, to charge just and reasonable rates or charges for such services, and to
obligate the owners, lessees, or occupants of all property served to  pay the cost of solid waste disposal
service  to their respective properties. These  rates or charges shall take into account the  character,
kind, and quality of the service and of the solid waste,  method of disposition, number  of people
served at each place of collection, and  all other factors that enter  into cost of service, including
interest  on principal,  investments, amortization of principal, depreciation, and other overhead
charges  upon facilities owned and operated by the municipality or later acquired for such  use.  Such
rates or charges when fixed may be billed in such manner as the governing body may determine, or
added to and collected with water bills or bills for sewage disposal  rendered to owners, lessees or
occupants of property.

SECTION 5. FIXING RATES; PUBLICATION OF ORDINANCE. Before any rates or charges  for
solid waste disposal service are fixed under the authority of Section  4, the ordinance establishing
such rates or charges shall be published or posted as by law provided,  and shall set forth the rates or
charges for each type of service,  and shall  contain a notice to all persons or parties interested that
the same will be considered at a public hearing not  less than three weeks from the publication  or
posting  of said ordinance as required by  law,  upon which date a public hearing shall be conducted
by the governing body  at which any person  affected by any rate or charge shall be given  an oppor-
tunity to be heard as to the rate or charge he will be called upon to pay.  The proposed ordinance
may be  amended by the governing body before enactment in any manner not inconsistent with the
terms of the notice of hearing thereon .  Said  ordinance and the rates or charges established therein
as proposed or as amended, shall take effect upon publication or posting of the ordinance  as required
by law, or at such later date as shall be fixed by such ordinance.  Like procedure shall be followed
before the  establishment of any change in such rates or charges.  Every ordinance upon enactment
shall be signed,  attested, filed, published or posted, and recorded  as provided by law for enactment
of ordinances.

SECTION 6. CHARGES; TAX LIEN ON LAND; COLLECTION.  The rates, or charges for solid waste
disposal service shall be a charge against the premises from which solid waste is collected, and the
owner,  lessee, or occupant of the premises, or against any or all  of them; and any such claim  for
unpaid rates, or charges which have been properly billed to the occupant  of the premises may  be
collected in a civil action  in any court of competent jurisdiction, or, in the discretion of the  govern-
ing body of the municipality, may be certified to the county auditor where the premises are located
with the taxes against such property served and shall be collected as other taxes are collected. Pay-
ments of deliquent charges  shall be credited to the fund as are current funds for that purpose, deduct-
ing therefrom any cost  of collection accruing to the municipality.

SECTION 7. CONTRACT  FOR SOLID WASTE DISPOSAL SERVICE  BY OTHERS AUTHORIZED

(1)  A municipality may provide solid waste disposal services by the use of its own forces and facili-
ties or may contract for such services to be furnished to the municipality upon such terms  and conditions
as the governing body may  determine in the public interest with any person, firm or corporation,
private  or public,  or with any other municipality, and by ordinance may obligate the owners,  lessees
or occupants, of all property served to pay the cost of such services to their respective properties as
provided under  Section 4.
(2)  The obligation incurred by any municipality in the making of any such contracts shall not  be
considered as a part of its indebtedness under the provisions of its charter, or by any law of this state
                                           IV-28

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 Document IV-4,  Page 4
 fixing the limit of amount of its indebtedness; nor shall it be required, at any time before making,
 or during the life of such contracts,  to have specifically provided for the same by previous  tax
 estimates or levy, or to provide for or have on hand in its treasury more money applicable to
 such contracts  than the amount to be paid thereon during a single year.

 SECTION 8.  SOLID WASTE DISPOSAL FUND.  The moneys received from the rates and charges
 as authorized by Section 4 shall be deposited  in a fund separate and distinct from any and all
 other municipal funds, to be designated  "Solid Waste Disposal Fund," which shall be a continuing
 fund to which shall be credited all receipts, and to which shall be charged all costs incident
 to such activity.  Moneys may be temporarily advanced to said fund from any available
 unencumbered  and unappropriated balance in  any other fund or funds, and as receipts permit,
 reimbursement  of moneys advanced from other funds shall be made.

 SECTION 9.  AUTHORITY TO DISPOSE OF LAND.  The governing body of a municipality after
 public hearing  upon notice given by publication or posting as by law provided may, upon
 determining that any tract of land or interest therein acquired under or subject to the provisions
 of Sections 1 to 15  is no longer needed for the purposes thereof, sell, lease, or otherwise
 dispose of such tract or interest upon such terms as it deems best in the public interest, or may
 provide for the use  thereof for other  purposes, so far as not inconsistent with any lawful
 restrictions on  the use or disposal of  such tracts or interest therein.

 SECTION 10.  EMINENT DOMAIN.  A municipality is  hereby authorized and empowered  to
 exercise the power of eminent domain for carrying out the provisions of Sections 1 to 15. Such
 proceedings shall be in accordance with	(list appropriate statute provisions or recite new
 provisions as required)	as now in  force or hereafter amended.

 SECTION 11.  GIFTS, GRANTS OR LOANS.   A municipality may, in its name and behalf accept
 gifts, grants or loans  of money or other property from  the United States, the state, or any other
 source for any purpose under Sections 1  to 15 may enter into any agreement for  repayment or
 otherwise required in connection therewith, and may  hold, use and dispose of such money or
 property for said purposes in accordance with the terms of the gift, grant, loan,  or agreement
 relating thereto.

 SECTION 12.  RULES AND REGULATIONS, METHODS, AND MINIMUM STANDARDS.   (1) A
 municipality may by ordinance establish rules, regulations, and minimum standards applicable
 to solid waste and land pollution which  rules,  regulations and standards shall meet at least  the
 minimum requirements established by the	(list appropriate state-regulatory agency  having
 responsibility).
 (2)  The governing body in providing for solid waste  disposal may by ordinance, or any amendment
 thereto, provide in what districts or  along which streets collection shall be made, and volume of
 solid waste to be collected, leaving  certain amounts or types of solid waste to private disposal,
 but shall continue to  have the authority to regulate the time and manner of private disposal, varied
 according to the nature of the solid waste accumulated and disposed of.  Such regulation may
 provide for immediate abatement of any condition which  is a menace to public health and safety.
 In such  cases notice may be  given to the owner or occupant of premises for the summary disposal
 of solid waste or unhealthy or unsafe condition by posting upon  the premises notice of what  is
 required.  If the notice be not obeyed within the time fixed  in said notice, the  municipality shall
 have the right to remove such solid waste or such unhealthy or unsafe condition, charging such
 rates or charges as are prescribed, or the cost  thereof, and shall have the right to collect the
 same as rates and  charges are herein  authorized to be  charged,  made and collected.  In  lieu of
such method, the  municipality may for adequate compensation by contract with the owner of any
 premises,  perform any service upon public or private property in the removal of solid waste,
 covering with proper filling  material  any foul, unhealthy or unsafe material,  including low grounds,
which are or may  become foul, unhealthy or unsafe.
 (3)  The governing body shall have the authority to direct the method of handling and storage of
solid waste on public  or private premises, to require the owner, lessee or occupant of the premises
 to place the same at the most convenient place upon the premises, and if convenience in the
 collection thereof requires containers on  premises for the  handling thereof,  the governing body may
 require  the same.
                                          IV-29

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 Document IV-4, Page 5


(4)  The governing body may adopt and amend ordinances regulating the use of disposal facilities.
Such ordinances may also establish standards which upon adoption shall govern the operation of
solid waste disposal facilities throughout the municipality, including those operated by the
municipality,  other public  agencies or by private operators.  Such regulations may apply to the
location of solid waste disposal facilities, requirements relative to the sanitary operation thereof,
requirements regarding the  equipment necessary relative to the amount of material being received
at the facility, requirements in relation to the control of salvage operations,  rodent control,
water or air or land pollution control,  and such other subjects as may be required for the public
health,  welfare,  and safety relative to the operation of such facilities.  The municipality may
issue permits or licenses for commercial private solid waste disposal facilities  and may require
that all  solid waste disposal facilities be registered with the appropriate municipal office.
Before acting  on an ordinance regulating the operation or location of solid waste disposal facilities,
the governing body shall hold a public hearing upon the proposal therefor upon at least three
weeks notice given by publication or posting as required by law, stating briefly the subject matter
and the general purposes of the proposed ordinance.  The proposed ordinance  may be amended  by
the governing body before enactment in any manner not inconsistent with the  terms of the notice
of hearing thereon.  Said ordinance, as proposed or as amended, shall take effect upon publication
or posting of the ordinance as required by law.  Every ordinance upon enactment shall be signed,
attested,  filed, published or posted, and recorded, as provided by law, for enactment of
ordinances.

SECTION 13.  VIOLATIONS,  PENALTIES.  Any municipality  is hereby authorized by ordinance
to impose penalties and provide for punishment for violation of any ordinance or regulation
relative to the accumulation of solid waste, its collection or  disposition.

SECTION 14.  JOINT COOPERATION.

(1) A municipality may be a party to a joint cooperative project, undertaking, or enterprise with
any one or more other governmental subdivisions or other public agencies for any purpose under
Section 2 upon such terms as may be agreed upon between the governing bodies or authorities
concerned.  Without limiting the effect of the foregoing provision or any other provisions of
Sections 1 to  15, a municipality, with respect to any of said purposes, may act under and be subject
to the provisions of	(Iowa Chapter 28E; or Nebraska Chapter 23, Article 22)	,
as now  in force or hereafter amended,  or any other appropriate  law now in force or hereafter
enacted providing for joint or cooperative  action between governmental subdivisions or other
public agencies.
(2) A municipality may, upon such terms as may be agreed upon with  the respective governing
bodies or authorities concerned, authorize the use by any other governmental subdivision or other
public agency of any facilities of the municipality constructed or used for  any purpose under Section
2 so far as the capacity thereof is sufficient beyond  the needs of the municipality.   A municipality
may expand any such facilities and permit the use thereof by persons,  firms,  corporations, private
or public, municipalities or other public bodies,  outside the municipality, so far as the  capacity
thereof is sufficient beyond the needs of the municipality upon such terms as the governing body
may prescribe.

SECTION 15.  POWERS ADDITIONAL

(1)  It is hereby found and  determined  that solid waste disposal  is a matter  of  statewide concern and
that the provisions of Sections 1 to 15  shall be independent of and in addition to any other  provision
of the laws of the State of (Iowa) (Nebr.) with reference to the matters covered hereby and shall be
considered as a complete and independent act and not as amendatory of or limited by any other
provision of the laws of the State of (Iowa)  (Nebr.)  The  purpose of these sections is to permit  any
municipality to engage in the activities hereinbefore authorized, and to promote the public health,
safety,  welfare,  convenience and prosperity of the municipality. The activity herein authorized
shall be considered a public utility and such activity may be merged and operated with any other
municipally operated utility, if deemed necessary and economical.  Accounting  for the activity
herein authorized shall be  separate as hereinbefore directed.
(2)  If any provision of sections  1 to 15 is held unconstitutional or invalid,  it shall not  affect the
other provisions.
                                           IV-30

-------
 other functions is limited to cities of twenty thousand or more population.
 Wo recommend this limit be  removed for cities and towns in Iowa where the
 city or town is  a member of an agency such as the one proposed here, and
 that agency has a total membership in excess of twenty thousand population,
 and the Agency is prepared to provide the services contemplated in 368.24.

•               J-J-    Collection of Garbage and Refuse in Iowa and Nebraska
 Counties .   There is no provision for the counties in Iowa or Nebraska to
 provide for the collection and disposal of garbage and refuse  in the unor-
 ganized parts of the county.  We recommend that  permissive state legisla-
 tion be passed in both states which allows counties to provide such collec-
 tion and disposal service in such portions of the county as the Board of
 Supervisors or Board of  Commissioners determine is needed and  to provide
 that a  schedule of fees may be established to pay for such services.

 Until such legislation  is provided,  it is possible that part of the unorganized
 portion of  the counties may be served on a voluntary basis.

                _c.    County Disposal of Refuse in Nebraska, Chapter 23
 of the Statutes recognizes the need for counties to provide refuse disposal
 facilities and grants authority necessary to provide the facilities.  These
 provisions were added in 1967, when the current general solid waste revi-
 sions were passed.

 In Iowa, Sections 332. 31 thru . 34,  the Statutes recognized the counties role
 in refuse disposal but they are not as broad as in  Nebraska and further, they
 work through the township which could become cumbersome with an Agency
 operated system. We recommend the Iowa statutes be broadened in a manner
 similar to  the Nebraska Statutes covering county refuse disposal and that  the
 county be authorized to act as a county, eliminating the provisions or re-
 quirement  to work through the township.

        3.      State Regulatory Agency.  The primary responsibility for
 maintaining the public health  standards for the disposal of solid waste must
 be borne by the local political jurisdiction in which the facility is located;
 whether it  be  a city, town,  village or county. This is an inescapable respon-
 sibility which is proper,  traditional and practical. In addition to public health
 matters which are matters of statewide concern, they should also  be concerned
with local matters such as  economy,  adequacy,  future capacity,  zoning,
 aesthetic considerations,  traffic,  rate schedules or fees, hours and days  of
 operation,  and others.

 The State has two areas of  responsibility in solid waste disposal.   First, they
 should assume a position  of leadership and assist  the local jurisdictions in
developing a competence  in those aspects of local  concern where this assistance
                                   IV-31

-------
is needed and requested.  Second, they should assume responsibility for estab-
lishing minimum technical provisions for solid waste disposal that may be
necessary to protect the public health,  as a matter of statewide concern.  The
matters  of local concern listed above are not suitable subjects for the state to
regulate.  Fees and zoning and other similar matters are the affairs of the
local community.   The state can  be helpful in these areas but  should not be
given any regulatory authority.  However, the state has  a definite  responsi-
bility to  safeguard public health,  in matters  of  statewide concern,  and solid
waste disposal certainly must be considered as falling within this category.
To maintain a separation between statewide and local matters, the state should
limit their regulatory authority to establishing  and enforcing the minimum
technical standards required to insure  sanitary disposal of solid waste.

In 1967,  the State of Nebraska placed the responsibility for proper solid waste
disposal in the State Health Department, and provided in Chapter 71,  Article  41,
the authority for the Director of Health to regulate this practice,  to set
standards,  and to license  disposal sites.  A  very modest staff was provided
to implement the provisions of the Article 41.   It  is expected that this law
will be highly effective in  improving solid waste disposal conditions in the
State.

There is no similar law in Iowa,  where the State  Health Department does not
have specific authority in  the field of solid waste  disposal.  Some progress
can be made under Iowa's general health laws and in specific cases where
water pollution laws can be invoked against improper solid waste disposal
practice  which is  causing  water pollution.  New air pollution laws  will soon
be available to apply to solid waste disposal facilities where open burning is
practiced.

We recommend Iowa add specific provisions to their statutes granting the
Department of Health specific authority to license, set minimum technical
standards,  and  regulate solid waste  disposal in Iowa.

In addition to  specific authority for the Iowa Health Department, both the  Iowa
and Nebraska Health Departments will  need to adequately staff their organi-
zation to implement the provisions of the law.  The scope of this  report  does
not include a study of the  staffing requirements of the state agency, but to
assure proper management of solid waste disposal in this Study  Area, the
periodic inspection by the state regulatory agency would be desirable.

We recommend a state inspector visit each disposal facility at least once
each quarter for the purpose of inspection for minimum technical  standards,
and to assist the facility's managers and operators in solving  disposal
problems.

We lurther recommend that both departments require all disposal facilities be
licensed by the  state.  As a condition for licensing, each applicant should be
required to submit detailed plans, prepared by a  professional engineer regis-
tered in that state.  The plans should include an area topographic plan, subsurface
                                    IV-32

-------
investigation, initial development of the site,  an operational plan,  and what-
ever other data the department may require.

.L        LOCAL LEGISLATION
          1 .       Disposal Ordinance.  The recommended public sanitary
landfill sites will be located in places under municipal jurisdiction.  Even
i hough these sites may be operated by a. non-profit governmental agency for
and on behalf of the counties and other municipalities, it is important that
these public sites and any private disposal activities come under the health
regulation of the jurisdiction in which the sites are located.  As an extra pre-
caution to assure that proper health conditions are maintained at all times,
each city, town,  village, or county should pass reasonable  but adequate regu-
lalions for all disposal activities conducted within their jurisdiction.

Because each municipality has a slightly different format for regulation,  and
has different provisions for licensing,  fees and inspection procedures; we
have prepared a typical Disposal Ordinance, patterned after a typical City
format.   This ordinance, which contains what we believe to be the essential
elements for such an ordinance,  is enclosed in this Part IV of the report
as Document IV-2.

Kach municipality should modify the recommended Disposal Ordinance to
conform to their local format and procedures,  and add to this ordinance any
local provisions necessary to  suit their form of government and any special
requirements which they deem necessary. They should also add specific
language designating who in their local governmental unit shall act as the
"Health Officer" who shall be responsible for the required administration
and enforcement.

          2.       Collection Ordinance.  A typical collection ordinance has
also been prepared, patterned after a typical city format.  This ordinance,
which contains what we believe to be the essential elements for such an ordi-
nance, is enclosed in this Part IV of the report as  Document IV-3.

Ff the Agency and certain municipalities wish to provide  a collection service,
(he ordinance can be used as a guide for the required ordinances.  If the
Agency does not offer  such a service, the ordinance may still be of some value to
ihe municipalities, as a guide  in the preparation  of an ordinance for their own
collection service.

Each municipality should modify this collection ordinance in a manner  simi-
lar to the modifications described in the preceding paragraphs concerning
the Disposal Ordinance.

          3.       Junked Automobiles. In Part II, Section D,  of this report,
(lie problems associated with junked motor vehicles are  discussed and local


                                   IV-33

-------
legislation is  recommended.  We have found that several communities in the
Study Area now have adequate local legislation to cope with the objectionable
aspects of this problem.  In general,  these laws are not fully enforced.

Zoning arid licensing laws should be enforced to assure  that commercial  auto
salvaging and scrap metal dealers operate their businesses in places zoned
for this activity and in accordance with licensing regulations.  This would
eliminate a substantial portion  of the  problems associated with this industry.
Where junked auto hulks  or inoperative vehicles are stored  on private property
and these vehicles are a  nuisance,  they can be controlled through an ordinance
which declares them to be litter.  Omaha Ordinance Section 25. 85. 050 states
"It shall be unlawful for a person to place,  cause  to be placed or allow to
remain on this property,  a motor vehicle or part  thereof which is in wrecked,
junked, partially dismantled, inoperative or  abandoned condition; provided,
however, that this Section shall not apply to any motor vehicle which is kept
in the operation of a business pursuant to any municipal ordinance or kept
a garage." Section 25. 85. 060 provides for the removal of such vehicles.

Council Bluffs has a similar ordinance and has used it effectively from time to
time.

K.       SANITARY LANDFILL STANDARDS
In the preceding Section J,  we recommended that each municipality in which
 a sanitary landfill is located adopt an ordinance controlling the disposal
of solid waste.  In the recommended Ordinance,  Document IV-2,
standards lor Sanitary landfills  are set forth in Section 3.  These standards con-
tain the essential elements for a first class type  operation which if enforced
would insure that such a disposal facility would be compatible with other land
use and urban living.

Some authorities have produced standards with lesser requirements for sites
not in an urban area.  In fact, we  have recommended from time to time in
other reports that different standards be  applied  to Urban, Isolated and Remote
areas.  In the Omaha-Council Bluffs Metropolitan Area, the four recommended
urban sites should certainly be constructed and operated to the  highest standards.
In the case of the one rural site in eastern Pottawattamie,  it is possible that
some requirements could be relaxed such as sight screening of the site; how-  •
ever, the requirements which could be relaxed are not  significant in the over-
all cost of the facility.  We recommend that all of the facilities be  constructed
and operated in a way to meet or exceed the standards listed above.

L.       ALTERNATE POSSIBILITIES
         1.     Organizational Structures.  There  are many organizational
 structures which could be used for the frame work  necessary for the safe and
 sanitary disposal of solid waste in addition to the bi-state public agency which
 is recommended.  Included in the possibilities  are  the following:
                                   IV-34

-------
              Individual Comrnunity Effort

        1.    Each community provide facilities for own use
either through own operation of facilities or agreement to use
neighbor's facilities.

        2.    Some communities may provide for joint use
of miscellaneous facilities through inter-local cooperation
Act of Nebraska and joint exercise of Government  Powers
of Iowa.

        3.    Some communities may use private enterprise
disposal facilities open to public for fee or community contract.

        4.    Any combination of 1, 2 and 3 above.

             Individual County Effort

        1.    Each county provide  facilities for use of county
residents and communities.

        2.    One county  provide for self and neighboring county
through agreement.

        3.    Some combination of counties providing  joint use
of miscellaneous facilities through Joint Powers Acts of Iowa
and Nebraska.

        4.    Private enterprise.

        5.    Any combination of 1, 2,  3 and 4 above.

                 Regional Effort

        1.    Form a Nebraska area regional organization to
provide facilities for Nebraska and an Iowa area regional organi-
zation to provide facilities for Iowa.

        2.    One state regional organization provide  for self and
other state regional organization through agreement.

        3.    Form a regional organization to provide for joint use
of facilities for entire two state Study Area through Joint Powers Acts
of Iowa and Nebraska.  (This is the recommended  plan).

       4.    Form a regional organization to prepare a regional
area solid waste plan.  Each county or  each community or
combination of counties and communities carry out own disposal
in accordance with plan.

       5.    Private enterprise.

                           IV-35

-------
                6.    Any combination of 1,  2,  3,  4,  and 5  above.

In general the individual efforts of the cities and to some extent the counties,
to provide facilities lor their own use,  would result in duplication  of facili-
ties,  equipment and management.  In most cases the  facilities would be too
small to be economical and too small to attract and afford professional manage-
ment.  The single exception to this fact would be the  City of Omaha.  This
city is large enough to operate large sites, without prohibitively high costs,
although the costs would exceed the costs contemplated in the joint agency
approach.

Joint  facilities to be  shared by various municipalities or contract arrange-
ments would be an improvement over strictly individual efforts but the same
disadvantages would  prevail except to  a leaser extent.  Again the exception
would be the City of Omaha.  If this city would provide  facilities for them-
selves and neighboring communities the efficiency could approach that of
the recommended agency.  The principal disadvantage to this arrangement
would be the political and jurisdictional problems which usually appear when
a giant city attempts to provide services to smaller neighboring communities.
This would be particularly true in the  location of sanitary landfill sites outside
the political jurisdiction of the large city.

Private enterprise could provide the required facilities,  however, there are
several serious flows in this concept.   As explained in  detail in Part III the
total cost of solid waste disposal is made up of two basic items, i.e.,  the
cost of hauling the waste  to a disposal facility and  the cost of operation of
that facility.  The proper location of the proposed  facilities, to produce the
lowest total cost, is  very important.   Private enterprise without the ability
to exercise the right of eminent domain could experience serious problems
acquiring the necessary property in the right general areas.

1'acilities  provided by private enterprise must pay taxes and are intended to
operate for a profit.   It can be argued and indeed it is often true that private
enterprise is more efficient than public agencies and  can make  a profit
charging the same fees.  This  is not necessarily true when a public agency
is provided with  adequate resources and is professionally managed.  The re-
commended agency should be able to operate in the same way as private
enterprise but will enjoy the very significant advantage of eminent domain,
uo taxes and no need to produce a profit.

         2.     Operation of Agency Facilities.  The  recommendation in  this
report contemplates  that all of the solid waste disposal facilities be owned
and operated by the agency using the agency's own forces and equipment.
As an alternate to this, the agency  could award contracts to private operators
to operate the facilities for the agency.  It would be necessary to prepare de-
tailed specifications  setting forth exactly what the  Contractor would be required
to do  and what the agency would be  required to do.  It would also be necessary
to prepare a new cost estimate to include taxes and profit for the Contractor.
                                    IV-3 6

-------
If the agency would desire to contract for the operation we would recommend
the agency furnish the land and capital improvements to the land, including
the initial development.  These improvements should be permanent and amor-
tized over a long period.

M.	FEDERAL PARTICIPATION.  The preparation  of this  study and report
wag financed partially with local funds from the MAPA, and partially through
a Federal Grant from the Office  of Solid Waste,  USPHS, Department of Health,
Education and Welfare.  This grant was authorized under the provision of the
"Solid Waste Disposal Act" which became law during the 89th Congress.
(PL89-272)

In the current session of the 91st Congress, there are bills in both the House
of Representatives and the Senate which offer amendments to the Solid Waste
Disposal Act.   Some  of the bills  are similar or identical to bills which died
in committee at the end of the  90th Congress.  Of particular interest to the
MAPA and the Agency are provisions  of "Grants for Construction".  Not only
are grants included but there are provisions for larger grants to organization
serving more than one community as contemplated in this  report.

Under these bills it would be possible for the Agency to receive up to 75% of
the  cost of construction of solid waste facilities, including completion and im-
provement of existing facilities.

Progress of these amendments should be carefully watched by the Agency Board
and the Director.  A  sizeable grant toward constructing and equiping the land-
fill  sites could considerably reduce the size of the revenue bond issue required
for  the Agency's initial operation.  This would,  in turn, also reduce the dis-
posal fees that  would be required.

It is not suggested that any of the improvements or  recommendations made in
this report be delayed pending the possibility of additional Federal Funds.  It
has been demonstrated that these improvements can be made and service im-
proved at a reasonable cost to the community.  However,  any additional method
of reducing these costs should not be overlooked as they might become available.
                                 IV-37

-------

-------
 DEPARTMENT OF
 HEALTH, EDUCATION. AND WELFARE
 PUBLIC HEALTH SERVICE
                                                          Forni Approved
                                                          Budget Buieau No. 68-.s>-6801<)
                                         COMMUNITY SOLID WASTE PRACTICES
                                LAND DISPOSAL SITE INVESTIGATION REPORT
 1..STATE
 4. NAME OP SITE
                             2. COUNTY
                             II   12   13
                                                  4   5   C
                                                             a. SITE LOCATION (Politica
                                        5. ADDRESS OF SITE
                                                                                                   7   «   a   10
                                                                               «.  DATE OF SURVEY
                                                                                    DAY     MONTH     YEAR
                                                                             _J	15  16	17   18	19   2O
 T. NAME OP PERSON COMPLETING PORM
                                                                      9. ORGANIZATION AND ADDRESS
 10. POLITICAL JURISDICTIONS SERVED BY LAND DISPOSAL SITE
                    NAME OP
             POLITICAL JURISDICTION
                                  21   22  Z»  24
                                  45   4«  47
                        ESTIMATED
                     PERCENTAGE OF
                       JURISDICTION
                     SERVED BY SITE
                            AVERAGE DISTANCE
                               OF SITE FROM
                            CENTER OF SOURCE
                                AREA (HIlea)
         FOR ADDITIONAL. ENTRIES. CHECK HERB
                                                (03)  AND MAKE ENTRIES IN ITEM *4S
                      II. SITE OPERATED BY



                         |  | PUBLIC AGENCY


                         |  | PRIVATE AGENCY
                                                                                          12. SITE OWNED BY
                                                                                             |  | PUBLIC AGENCY
                                                                                                PRIVATE AGENCY
 1«. IS OPERATION
    REGULATED BY A

    HEAL1M AUTHORITY?
YES

NO
IF YES. INDICATE LEVEL
OF PRINCIPAL AUTHORITY
    (Chock cne only)
[77J COMMUNITY   |   [STATE
I77J COUNTY      ||OTHER.

PJ QUARRY OR BORROW PIT Q HILLSIDE
PI GULLY-CANYON [~l MARSH. TIDELAND
™ — OR FLOOD PLAIN
| 	 1 LEVEL AREAS
(Specify) Do
IB. ZONING/ LAND USE SURROUNDING FACILITY (Chuck predomi
ZONING
L J NONE [77J INDUSTRIAL
[7J«£SIDENTIAL [77J AGRICULTURAL
PI COMMERCIAL 1 1 OTHER


15. YEAR SITE PLACED IN OPERATION
16. ANTICIPATED LIFE REMAINING (Yeara)
17. TOTAL AREA OF SITE (Acne)
<•• AREA TO BE USED FOR LAND
DISPOSAL (Acne)
19



61

04 6V



59

O2

06


00

63

07

6Q 69 70 71
nant type only)
LAND USE
LJRES.DENTIAL [^AGRICULTURAL
0 COMMERCIAL n OTHER

1 I INDUSTRIAL
(Specify)


72 73
20.  HUSEOF      riYES    IFYES.CHECK  PI RECREATIONAL  ,	.LIGHT          .	|A(3R|r.11T11BF  r—lUSENOT
                  1   '                       <—IAREAORPARK  I—ICONSTRUCTION  I—(AGRICULTURE  \—|DETEHMINED
    COMPL.CTED               PREDOMINANT
    SITE PUANNEDT f  1 NO     USE ONLY       P"] PARKING LOT    p~] HEAVY          I ~1 OTHER 	      	
                  '   '                       '—'                '—'CONSTRUCTION  '—!UIMtK	fSjiiijy)	
21.
23.
WILL PUBLIC AGENCY CONTROL
COMPLETED SITE USE*
FREQUENCY
OF COVER
(Chock one on/y)
LJ NONE
[J~] DAILY
r;
r~

(End of each
working day)
J YES

[-ZJ DAIL
1 lOTH
22.
MATERIAL US
FOR COVER
(Chock one cni
Y (Except face)

(Specify)
ETi T— -T ..^ i 	 1 —-~..__ ~~~
[ 1 EARTH


24. IS SPREADING ANO COMPACTION I 	 |YES 1
[ "1 NO L_-


7e

7«
                                        3T BE USED BECAUSE OF WEATHER CONNECTED CONDITIONS (Enter are'
                                                                                                per
                                                                      .ratfe T  T   I
                                                                      >~>L_LJ
2A. GENERAL CHARACTER OP OPERATION (Judgment evaluation -chock appropriate categories)
APPEARANCE


[7 J SIGHTLY




T J UNSIGHTLY
16


CONTROLLED?

HYES
F:INO
„







CONSIDERED TO BE
A NUISANCE?
Q]YES
a NO
»r
ROUTINE BURNING

[ | NONE
PJ UNCONTROLLED
a PLANNED AND
LIMITED
"1
ARE THERE SUR-
FACE. DRAIN AG
PROBLEMS?
LU YES
LTJNo
IB
E




ARE THb-RE
LEACHING
PROBLEMS?
Til YES
a NO
20





|
N i i - I - 1 2 B - ,>  (ClN)(4-tin)
                                              Exhibit  1-1  Page  1

-------
                             LAND DISPOSAL SITE I NVESTIGATION REPORT (Page 2)


RODENT CONTROL
PROGRAM
FLY CONTROL
PROGRAM
BIRD CONTROL
PROGRAM
DUST CONTROL
PROGRAM
ODOR CONTROL
PROGRAM
NEEDED
PROVIDED
NEEDED
PROVIDED
NEEDED
PROVIDED
NEEDED
PROVIDED
NEEDED
PROVIDED

KEPT IN ANY FORM? ' 	 '

YES I NO
Cl
1
n
n
n
L
E'J
a
i — i

n »
n 2
n *
n *
n 2
n *
n »
a -
[ 1 2
[~1 3

Do
[^] NO not

TONS WEIGHED ' ... "
TONS ESTIMATED
CUBIC YARDS
30. GENERAL CLASSIFICATION



Do
no(
utto
1
2
3

4
H

a
7
s
0
0



JJ_L1_


-1 OF SOLID WAST
1 TE (Chmck those







ES
tccep(ed)
| (HOUSEHOLD ( ]TNf^^ LZ]INST'TUTIONAL
70 72 74
riCOMMERCIAL [~|ASf"CUI-- (— 1 1 NCIN ER ATOR
V, L-JTURAL L_J RESIDUE ONLY
38, EQUIPMENT AVAILABLE
(Average ullltxed dalltf
DRAGLINE OR SHOVEL-TYPE EXCAVATORS


SCRAPERS (Self-propelled)
TRACTORS (Track or Rubber Tire)
(Bulldozer or Hlfh Lilt Loader)
TRUCKS


Do
not
use

43
Do 1
OTHER not |
(Specify) use
^
NUMBER

?5

37

39



36

38

40


44 45


JI7...W

28. IS LOWEST ART F \__\ [_ 1
20. FIRE [~]NONE | [WATER
PROTECTION 	 	
IFIRFRPFAK BOTHER
• 	 (Specity)
30. NUMBER OF TIMES FIRE CONTROL EQUIPMENT

31.
IS SALVAGING PERMITTED' CD YES D NO
32.
IS SALVAGING PRACTICED' [~^j YES d] NO
33. ESTIMATED NUMBER OF LOADS DEPOSITED DAILY (Average)
f ROM OTHER VEHICLES
FROM PUBLIC FROM PR VATE
COLLECTION COLLECTION
VEHICLES VEHICLES (Specify)

-------
                              LAND DISPOSAL SITE INVESTIGATION REPORT (Page 3)
 45. CONTINUATION ITEMS
   ITEM NO
                                                  ADDITIONAL INFORMATION
46 REMARKS (Attach addition*! nhnet It necessary)
NCU1.120-2  (CINJ,4-68)
                                        Exhibit 1-1  Page  3

-------
          TENTATIVE RATING METHOD  FOR SANITARY LANDFILL OPERATIONS
                                                     This item shall be rated as follows:
ITBiM I:  Access Road.  Access roads shall
be designed and constructed so that traffic
will flow smoothly and will not be interrupted
by ordinary inclement weather.

Reason.  In order  to avoid needless expense,
it is of the  utmost  importance that collection
vehicles are not delayed at the disposal site
and that all refuse is  unloaded only at the fill
area.  Since the refuse  hauling operation is
unproductive time  for the  refuse collectors,
any unnecessary delays are costly and can
result in unfinished collection routes.

   This item shall be rated as follows-.

   If an all-weather access road, negotiable
   by loaded collection vehicles, has been
   provided to the  entrance of the landfill.
                                   3 points

   If the access road provided is negotiable
   under most conditions and an alternate
   site is located so as  to provide for the
   sanitary disposal of  refuse during incle-
   ment weather.
                                   2 points

   If the road is negotiable in good weather
   only and no alternate site is provided.
                                   0 points

ITEM 2:  Employee Facilities.  Suitable
shelter and sanitary facilities shall be
provided for personnel.

Reason.  Shelter is a desirable protection
of the landfill employees during inclement
weather. Toilet and  handwashing facilities
are desirable for good personal hygiene for
landfill employees and collection personnel.
Better working conditions contribute to
employee morale and retention.
   If permanent or temporary shelter of
   adequate size is provided, along with
   safe drinking water, sanitary handwashing
   and toilet facilities, suitable heating
   facilities, screens,  and electricity (if
   needed).
                                  3 points

   If temporary shelter is provided with
   suitable heating facilities, screens,  and
   an approved portable toilet.
                                  2 points

   If no shelter and toilet facility is
   furnished.
                                  0 points

ITEM 3:   Measuring Facilities.  Provision
shall   be made for weighing or adequately
measuring all refuse delivered to and dis-
posed in the sanitary landfill.

Reason.  A suitable method of measuring
incoming and/or deposited refuse is desir-
able to provide a reliable quantity of data, to
determine  trends and to estimate future
needs.  Estimates of volumes based on
truckloads rather than weights are mislead-
ing.  Weighing provides the best basis for
establishing fees requiring scales as an
integral part of the sanitary landfill operation.
Weighing discourages trips to the site with
half-filled trucks. Determination of the volume
increments in deposited refuse may be done
by periodic volumetric surveys,  permitting
evaluation of the use-rate  and remaining
capacity of the site.

   This item shall be rated as follows^

   If suitable fixed or portable scales have
   been installed at the sanitary  landfill and
   are used continuously or if the landfill  is
 Not for General Distribution
 Subject to Revision
*Solid Waste Branch, Training Institute, EGA
                                                                  SW. SL. rm. 3R. 2.66
                                 Exhibit I-Z  Page  1

-------
Ti-nlativo Rating Method _fpr Sanitary Landfill Operations
    routinely "cross-sectioned""' to determine
   volumes in place (routine - each 30 days
   minimum).
                                   2 points

   If a scale is located on the way to the site
   (such as transfer stations) and is in con-
   tinuous use.
                                   1 point

   If no weighing is accomplished and  routine
   measurements of volume in place are not
   taken (each 30 days minimum).
                                   0 points

ITEM 4:  Communications.  Telephone or
radio communications shall be provided at
or near the sanitary landfill site.

Reason.   Communications are desirable at
the generally remote sanitary landfill  sites,
in case of emergency.  If the sanitary land-
fill is part of a combined collection and dis-
posal system, good communications will
result in better performance throughout the
system.

   This item shall  be  rated as follows:

   If reliable telephone or radio communi-
   cations arc installed at the site.
                                   2 points

   If communications are located within three
   miles and a suitable vehicle  is available
   at the site at all times.
                                   1 point

   If communications  are greater than three
   miles distant.
                                   0 points

ITEM 5:  Fire Protection.  Suitable measures
shall be taken to prevent  and control fires.
Open burning shall be  prohibited.

Reason.   Fires endanger life and property.
Smoke and odors create nuisances to surround-
ing property owners,  endanger  disposal
*An Engineering Survey procedure to deter-
mine volume increments, in place,  in the
filled portion of the landfill.  Convenient
benrh marks should be established.
personnel, and interfere with landfilling
operations.  Fires on sanitary landfills
cause them to revert to a status equivalent
to open dumps.

   This item shall be rated as follows:

   If an adequate supply of water under
   suitable pressure is available with neces-
   sary hose, etc,;  a stockpile  of earth
   is maintained reasonably close to the
   working face of the fill for smothering
   fires; a  suitable  fire extinguisher  is
   maintained on all equipment  and in all
   buildingte; and open burning is prohibited.

                                  3 points

   If the site has a stockpile of  earth reason-
   ably close to the  working face of the fill
   and open burning is prohibited.
                                  2 points

   If fire protection is not present or open
   burning is allowed.             0 points

ITEM 6: Limited Access.   Access to a
sanitary landfill shall be limited to those
times when an attendant-is on duty and only
to those authorized to use the site for dis-
posal of refuse.

Reason.  If public use of a sanitary  landfill
is allowed  when no attendant is  on duty,
scavenging, burning and indiscriminate
dumping commonly occur.  Men and equip-
ment must then be diverted from operations
to restore  sanitary conditions.  When access
to the site  during  operating hours is limited
to those authorized, traffic and other
accident hazards are minimized.

   This item shall be rated as follows:
   If access by unauthorized vehicles or
   pedestrians is prohibited.
                                  3 points

   If access is prohibited except during
   working hours.
                                  2 points
   If access is uncontrolled.
                                  0 points
                                Exhibit 1-2  Pa»e  2

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                                    Tentative Rating Method  for Sanitary Landfill Operations
ITEM 7:  Unloading.  Unloading of refuse
shall be restricted and controlled.

Reason.  For proper operation, systematic
placement of refuse,  restricted to a small
unloading area and coordinated with spreading
and compacting is required.  Controlled un-
loading reduces work, conserves  landfill
volume, permits better compaction,  mini-
mizes  scattering of refuse and expedites
unloading of collection vehicles.

   This item shall be rated as follows:

   If unloading is controlled and the unloading
   area is restricted to a minimum.
                                   2 points

   If adequate unloading directions are
   clearly set forth by legible signs, if an
   unloading  supervisor is on hand most of
   the  time and unloading is performed in
   a satisfactory manner.
                                   1 point

   If unloading is uncontrolled or  if the un-
   loading area is too large for adequate
   compaction and daily cover.
                                  0 points

ITKM 8:  Size of Working Face.   The working
face of a sanitary landfill shall be confined
enough to be  easily maintained with available
equipment.

Reason.  A large working face increases the
area to be compacted and covered with con-
current high  cost, delay and difficulty in
controlling fires.

   This item shall be rated as follows:

   If the 'size of the working face is small
   but is adequate for the collection vehicles
   to unload promptly.
                                   2 points

   If the working face 'is larger than the
   estimated minimum area required.
                                  1 point

   If the working face is much larger than
   necessary and/or  the dumping  is
   uncontrolled.
                                  0 points
ITEM 9:  Blowing latter.  Blowing litter
shall  be controlled by providing fencing
near the working area or by use of
earth banks or natural barriers.  The entire
landfill site shall be policed regularly and un-
loading shall be performed so as to minimize
scattering of refuse.

Reason.  The purpose of the sanitary landfill
is to dispose of the refuse in a sanitary
nuisance-free manner.  If papers and other
light materials are scattered and the area is
not policed, fire hazards, nuisances, and
unsightliness  result.

   This item shall be  rated as follows:

   If fences, artificial or natural obstruc-
   tions,  control blowing litter and the land-
   fill and surrounding areas are routinely
   policed to minimize litter at all times.
                                  4 points
   If some control of blowing litter  is
   exercised and all litter-at the landfill
   and/or immediate  area is policed at a
   minimum interval  of once each twenty-four
   hours.                          2 points

   No control of blowing litter is exercised
   and the site or the immediate area is
   commonly littered.
                                  0 points
ITEM 10:  Spreading  and Compacting of
Refuse.  Refuse shall be spread and com-
pacted in shallow layers, not exceeding a
depth of two feet of compacted material.

Reason.  Successful operation of a sanitary
landfill depends upon adequate compaction.
of the refuse.  Settlement will be excessive
and uneven when the refuse is not well com-
pacted.  Such settlement permits the ingress
and egress of insects and rodents and
severely limits the usefulness of the finished
area.

Compaction is best initiated by spreading
the refuse evenly in shallow layers rather
than placing the material in a single deep
lift.  Further compaction is provided by the
repeated travel of landfill equipment over the
layers and,  if necessary, by the use of
special compacting equipment.  Additional
compaction also can be achieved by routing
collection trucks so that  they travel
                                Exhibit 1-2 Page 3

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Tentatiy collating Method  for Sajiilary Landfill Operations
 repeatedly over the covered portion of the
 fill.  These procedures result in the greatest
 compaction and the least ultimate settlement,
 providing the most useful finished fill and
 best utilizing the capacity of the site.

   This item  shall be rated as follows:
   If refuse additions are spread evenly by
   repeated passages of landfill equipment,
   each layer being compacted thoroughly
   to a depth not to exceed two feet.
                                   5 points

   If the refuse is  spread but not adequately
   compacted into  a solid mass.
                                   2 points

   If the refuse is  neither spread nor
   compacted.
                                   0 points

ITKM  11:  Depths of  Cells in Fill.   Individual
cells in sanitary landfills shall be no greater
than eight feet in thickness.
          The total depth of a landfill is
governed by the characteristics of the site,
I he desired elevation of the completed fill,
and good engineering practice.  Construction
of a fill in well- compacted cells of not more
than eight feet each in thickness minimizes
settlement, surface cracking, odor release,
and offers increased fire protection.  Fills
using cells  thinner than eight feet do not
generally make maximum use of available
land,  but provide for earlier  reuse  of the
site.
   This item shall  be rated as follows:

   If fill is  constructed of properly  spread
   and compacted cells to a total thickness
   of eight feet or less.
                                   5 points

   If  fill is  constructed  of properly spread
   and compacted cells  to a total thickness
   more than eight feet but less than  12 feet.
                                     2 points

   If fill is  constructed without  compaction
   or in  cells exceeding 12 feet in thickness.
                                   0 points
ITEM 12:  Daily Cover.  A uniform compacted
layer of at least six inches of suitable cover
material shall be placed on all exposed
refuse by the end of each working day.

Reason.  Daily covering of the refuse is
necessary to prevent fly and  rodent attrac-
tion, blowing litter,     production of odors,
fire hazards, and an unsightly appearance.
Fly emergence generally is prevented by six
inches of compacted soil.   Daily covering
divides the fill into "cells" that limit the
spread  of fires within the fill.

   This item shall be rated as follows:
   If the cover material has the working
   properties of "sandy loam" as classified
   by the U. S. Department of Agriculture
   (USDA) and is compacted in an unbroken,
   uniform layer no less than six inches in
   de?th-                          20 points

   If the cover material is  a  soil having
   working properties less than the sandy
   loam specified and is well-maintained as
   above.                          , _   .  ,
                                   15 points

   If the cover material is  inert incinerator
   residue and is thoroughly  compacted to
   a uniform depth of no less than six inches
   and there are no rodent, insect,  or odor
   problems resulting.
                                 10 points

   If no daily cover is performed (any ex-
   posure of refuse after the  working day),
   or if daily cover is improperly applied
   (not  compacted; unsuitable material;
   nonuniform depth or depth less than six
   inches;  voids in cover; or  insect or rodent
   ingress or egress).
                                  0 points

ITEM 13:  Intermediate Cover.  In all but
the final lift of a landfill, a layer of suitable
cover material, compacted to a minimum
uniform depth of one foot shall be placed
daily on all surfaces of the  fill except those
where operation will continue on the  following
working day.
                                 Exhibit 1-2  Page 4

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                                    Tentative Rating Method  for Sanitary Landfill Operations
jteason.  More than one foot of soil cover
might be  wasteful in a landfill in which there
Is a clear intention to provide at least one
additional lift within one year.  Under such
circumstances,  a one-foot layer of properly
compacted and maintained cover will prevent
health hazards or nuisances until the next
lift is placed.

   This item shall be rated as follows:

   If the intermediate cover material has the
   working properties of sandy loam as de-
   fined by USDA  and is compacted to a
   minimum uniform depth of one foot.
                                    4 points
   If the intermediate cover material is a
   soil having working properties less than
   the sandy loam specified and is compacted
   to a  minimum uniform depth of one foot.
                                    3 points


   If the intermediate cover material is inert
   incinerator residue compacted to a mini-
   mum uniform depth of one foot.
                                   1 point

   If no intermediate cover is applied or if
   it is  improperly constructed causing odor
   and vector problems.
                                  0 points

ITEM 14: Final Cover.  A uniform layer of
suitable cover material compacted to a mini-
mum depth of two  feet shall be placed over
the entire surface of each portion of the final
lift, not later than one week following the
placement of refuse within that portion.

Reason.  A minimum final cover of two feet of
compacted suitable cover material will pre-
vent emergence of insects from the compacted
refuse,  minimize escape of odors and gases,
and prevent rodent burrowing.  This cover
also provides an adequate bearing surface
for vehicles, and  sufficient thickness for
cover integrity in the event of settling or
erosion.

   This item shall be rated as follows:

   If the final cover material has  the working
   properties of sandy loam as classified by
   the USDA and is compacted in a uniform
   unbroken layer with a minimum depth of
   two feet-                         4 points
   If the final cover material is a soil having
   working properties less than the sandy
   loam classification, compacted in uniform
   unbroken layer with a minimum depth of
   two feet.
                                    3 points

   If the final cover is incinerator residue;
   if no cover is provided  or if the cover
   provided is improperly constructed,
   resulting in odor, rodent and insect
   vector problems.
                                  0 points

ITEM 15:  Equipment Maintenance Facilities.
Provisions shall be made for the routine
operational maintenance of equipment at the
landfill site and for the prompt repair or
replacement of landfill equipment.

Reason.  Equipment breakdowns of a day or
more result in the  accumulation of uncovered
refuse (as in an open dump) with all  the
attendant health hazards or nuisances.
Systematic, routine maintenance of equip-
ment reduces repair costs, increases life
expectancy, and helps to prevent breakdowns
that  interrupt landfill operations.   In the
event of breakdown, prompt repair of equip-
ment, or immediate procurement of  stand-
by equipment  will  materially reduce  down
time.  Prompt repair of equipment and
availability of standby equipment insures
continuity of operations.

   This item shall  be rated as follows:

   If complete maintenance facilities and
   personnel are provided at the disposal
   site or  if standby equipment of suitable
   capacity and  capability  is available at all
   times.
                                  2 points

   If facilities for routine  maintenance are
   available on-site and if adequate provisions
   for major maintenance  and  repair have
   been made.
                                  1  point
                                 Exhibit 1-2  Page 5

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  Tentative H/itin^' Mrlhod for Samtnry Landfill Operations
   If maintenance facilities and repair pro-
   visions are not provided or are inadequate;
   if equipment is inoperable or of limited
   capability because of poor maintenance.
                                   0 points

ITEM 16: Sewage_Solids or Liquids and Other
Ha"drdous Materials   So wage solids or
liquids (septic tank or cesspool pumpings
and sewage  sludge and grit), and other
hazardous materials shall be disposed of in
a sanitary landfill only if special provisions
are made for  such disposal.
Reajion^ Sewage solids or liquids are in-
fectious and create health hazards if not
properly handled.  Other materials,  including
oil sludges, waste chemicals,  magnesium
shavings, and empty insecticide containers,
may also present special hazards. Unless
properly handled, these wastes can be danger-
ous to landfill employees.  When the  design
of sanitary landfill includes special provisions
for disposal of hazardous materials,  they can
be disposed of safely and need not be excluded.

   This item shall be rated as follows^

   If suitable procedures are established and
   followed for disposal of hazardous
   materials.
                                  2 points

   If all hazardous materials are excluded
  from the fill.

                                  1 point

   If hazardous materials are accepted
   without provision for suitable disposal.
                                  0 points

ITEM 17:  Large or Bulky Items.  Special
provisions shall be made for the disposal of
large,  heavy, or bulky items at small land-
fills or at landfills operated with light
equipment.

Reason.  Some special method may be neces-
sary for the disposal of such large items as
car bodies; refrigerators; water heaters;
large tires; some demolition wastes; and
large tree stumps, trunks, and branches.
Some of these items are noncombustible,
and it may not be advisable or permissible
to burn some of the combustible materials.
At landfills with heavy equipment,  such items
generally can be handled routinely with other
refuse; however, special provisions are
necessary to incorporate large or bulky
items into the fill at small landfills or at
landfills operated with light  equipment,

   This item shall  be rated as follows:
           i
   If approved special techniques are em-
   ployed to dispose of bulky items  and all
   disposal is done in an orderly and neat
   manner or if adequate disposal of bulky
   items can be obtained in the routine
   filling operation.
                                  3 points

   If bulky items cannot be handled  or are
   handled improperly.
                                  0 points

ITEM 18:   Burning. No garbage or refuse
containing garbage shall be burned at the
sanitary landfill.  Burning of select materials
shall   be  severely restricted, and shall be
conducted only  with the permission  of the
appropriate authorities.

Reason.  Garbage cannot be burned without
nuisance except in high-temperature inciner-
ators.  Any other method of combustion
creates odors,  air pollution,  and fire  and
safety hazards.   Such burning adversely
affects public acceptance of the operation
and proper location of future  sanitary  land-
fill sites.   Controlled burning of certain
combustible materials not  readily incor-
porated in the fill,  such as lumber, brush,
and tree stumps, may provide a satisfactory
means of disposal of these materials at
some isolated sites.

   This item shall be rated as follows:

   If no burning is allowed at any time.
                                  3 points
                                Exhibit 1-2 Page 6

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                                   Tentative Rating Method  for Sanitary Landfill Operations
   If burning of refuse is uncontrolled or is
   performed without knowledge of,  or per-
   mission by the local authority.
                                  0 points

ITEM 19:  Salvage.  When  salvaging is per-
mitted,  it shall be so organized that it  will
not interfere with prompt sanitary disposal
of refuse nor create unsightliness or health
hazards.  Scavenging shall not be permitted.

Reason.  Nothing  can be tolerated that
interferes with prompt sanitary disposal of
refuse.  When improperly  conducted,  salvag-
ing delays landfilling operations and creates
insanitary conditions.   The accumulation of
salvage at the disposal site often results in
vector problems and unsightliness, which
are deterimental to public  acceptance of the
operation.  Scavenging is an unhealthy,
aesthetically-objectionable practice that in-
terferes with the orderly and efficient opera-
tion of a landfill.

   This item shall be rated as  follows:
   This item shall be rated as follows:
   If vector control is not needed.
   If no salvaging is allowed.
                                  3 points
   If salvaging is controlled and all salvage
   is removed from the site at the  end of
   each working day.
                                  1 point

   If scavenging is  allowed or if salvage is
   allowed to accumulate beyond the end of
   the working day.
                                  0 points

ITEM 20:  ^Vector Control.  Conditions un-
favorable  for the production of insects and
rodents shall be maintained by carrying  out
routine landfill operations promptly in a
systematic manner.  Supplemental vector
control measures shall be instituted when-
ever necessary.

Reason.  While operation of a sanitary land-
fill according to these standards will  reduce
insect and rodent problems to a minimum,
any lapse  in proper operating procedures
may  result in attraction and rapid production
°f insects and rodents.  Supplemental vector
control measures may occasionally be neces-
sary to prevent health hazards or nuisances.
                                  2 points
   If vector control is promptly supplied
   when conditions warrant such control.
                                  1 point

   If vector control is needed or is not
   promptly furnished.
                                  0 points

ITEM 21:  Dust Control.  Suitable control
measures shall be taken wherever dust is
a problem.

Reason.  Excessive dust slows operation,
creates accident hazards and aesthetic
problems,  and may cause eye irritation or
other injury to landfill personnel.

   This item shall be  rated as follows:

   If dust control  is not required or if suit-
   able control measures are applied as
   needed.
                                  2 points

   If dust control  is applied as needed but
   is not effective.
                                  1 point

   If dust control  is necessary and is not
   applied.
                                  0, points

ITEM 22: Placement  in Ground Water.  The
depositing of refuse in locations where con-
tinuous or intermittent contact occurs be-
tween refuse and the ground water table
shall be  avoided.

Reason.  Gross contamination of underground
water supplies can occur in. areas where
refuse is in intimate contact with the water
table.

   This item shall be  rated as follows:

   If the  refuse is placed where the ground
   water table will not come in
   contact with the refuse, as determined
   by competent engineering authority.
                                  5 points
                                Exhibit 1-2  Page  7

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Tentative Rating Method  fqr Sanitary Landfill Operations
   "if intermittent contact with the ground
   water table may occur but adequate pro-
   visions have bi'on made to monitor the
  ^adjacent ground water quality and make
   appropriate operational changes, if
   indicated.
                                   3 points

   If refuse is deposited in water or where
   ground  water may come in intermittent
   contact with the refuse  and no provisions
   for monitoring have been  made.  „
                                   0 points
ITEM  23:  Drainage of Surface Water.  The
entire site, including the fill surface, shall
be graded  and/or provided with drainage
facilities to minimize run-off into and onto
the fill,  prevent   erosion or washing of the
fill,  drain off rain water falling on the fill,
and  prevent   the collection of standing
water.  The final surface of  the fill shall be
graded to a slope of at least  one percent,
but no surface slope shall be so steep as to
cause  erosion of the cover,

Reason.  Run-off from lands adjacent  to the
fill and rain falling on the fill may, unless
diverted,  percolate into the fill and pollute
the ground or surface water  with the leachate.
The  cover may be removed by erosion of the
fill and standing water may permit mosquito
breeding or may interfere with access,  un-
loading,  compacting or placement of cover.

   This item shall be rated as follows:

   If surface waters are diverted from the
   fill and no permanent ponding occurs.
                                   6 points

   If only occasional scouring or ponding
   of surface water occurs.
                                   4 points

   If surface drainage is not  controlled or
   is inadequately controlled.
                                   0 points

ITEM  24:   Final Grading.  The completed
fill  shall  be graded to serve the purpose
for which the fill is ultimately planned.  The
surface drainage  shall be consistent  with
the surrounding area.  The finished construc-
tion  shall not in any way cause interference
with proper drainage on adjacent lands nor
shall the finished fill concentrate run-off
waters into adjacent areas.  Seeding of
finished portions with appropriate grasses to
promote stabilization of the cover shall be
performed.
Reason. To promote sanitary landfill as an
acceptable refuse disposal practice,  and to
enhance the obtainment of appropriate future
sites,  it is important that the fill not only
be operated in an acceptable manner, but
also that the completed landfill blend with
its surroundings and, if possible, be utilized
for some purpose.

   This item shall be rated as follows.^

   If   completed portions of the landfill
   are properly graded and permit proper
   drainage.
                                 4 points

   If finished portions evidence some pond-
   ing uneveness or scouring correctable by
   proper maintenance.
                                 2 points

   If finished surfaces are not smooth and
   are improperly drained.
                                 0 points

ITEM  25:  Animal Feeding.  All animals
shall be excluded from the site.

Reason.  Consumption of raw garbage by
hogs is an important factor in the trans-
mission of trichinosis in man, as well as
trichinosis, hog cholera,  and vesicular
exanthema in hogs, therefore, hogs  should
be excluded from landfills.  Domestic or
wild animals will interfere with the  land-
fill operation.  Appropriate fencing  will
exclude animals and prompt covering of
refuse will make the site less attractive
for gulls and other birds.

   This item shall be rated as follows:

   If no animal feeding is allowed and proper
   fencing is installed, if needed.
                                 2 points
   If any animal feeding is allowed.
                                 0 points
                                 Exhibit 1-2  Page  8

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                                   Tentative Rating Method for Sanitary Landfill Operations
ITEM 26: .Accident _Prey_ont ion and Safety^.
Employees  shall be instructed in the prin-
ciples of first aid and safety and in the
specific operational procedures necessary to
prevent accidents, including limitation of
access.  Accident precautionary measures
shall be employed at the site.   An adequate
stock of first-aid supplies shall be  maintained
at the site.

Reason. The use of heavy earth-moving
equipment,  the  maneuvering of collection
trucks and other vehicles,  and the infectious,
explosive or flammable items that may be in
.he refuse can create accident hazards at
landfills.  The remote location of some land-
fills makes it particularly important  that
personnel be oriented to accident hazards,
trained in first-aid, and provided first-aid
supplies.  For reasons of safety, access
should be limited to those authorized to use
the site for the  disposal of refuse,

   This item shall be rated as follows-^

   If employees are given periodic safety
   training; and if an adequate  first-aid kit,
   and at least one employee trained in first-
   aid,  is available on the  site at all times.
                                   2 points

   If employees are given periodic safety
   training; and if an adequate  first-aid kit
   is available  at the site and trained first-
   aid assistance is available at a location
   within 3 miles of the site to which appro-
   priate communication is available,
                                   1 point

   If employees arc not given periodic safety
   training; or  if neither an on- site first-aid
   kit nor trained first-aid assistance (with-
   in 3 miles) is available.
   If no positive accident prevention program
   is  employed  or if unsafe practices ara
   carried on at the site.
                             Deduct 5 points
 IT KM 27:  Operational Records and Plan
 Execution.  A daily log shall be maintained
 by the sanitary landfill  supervisor to record
 operational information, including the type
 and quantity of refuse received, the portion
of the landfill used, and any deviations made
from the plans and specifications.  A copy
of ihe original plans and specifications, a
copy of the daily log,  and a plan of the  com-
pleted landfill shall be filed with the local
governmental agency  responsible for main-
taining  titles to land.

Reason.  Completed landfill sites are ulti-
mately  utilized for a variety of purposes.
When .he ultimate use of the site is known
beforehand, the landfill operation can be
planned so that suitable building sites,
roads,  &nd ,utilities, can be provided.  Final
grades  can be established and allowances
made for landscaping and adequate drainage.
A record of the construction of the landfill
ia necessary for the most efficient utilization
of the completed landfill site and for  the
prevention of health hazards or nuisances.

   This item shall be rated as follows:

   If complete records are maintained  as
   delineated above.
                                   2 points

   If the records kept are considered ade-
   quate for the intended use of the fill.
                                   1 point
   If there are no records.
                                  0 points
   If the sanitary landfill deviates materially
   from the approved plan in such a manner
   as to produce an unsatisfactory sanitary
   landfill (during operation or upon com-
   pletion)  or if a sanitary landfill is con-
   structed or operated without planning so
   as to elicit valid adverse comment  from
   the adjacent property owners and/or
   governmental officials.
                                 DEDUCT
                                 20 points

Suggested Method of Applying the Point
Ratings.

A summation of the points awarded for each
of the twenty-seven items yields a possible
score of up to 100.  The sanitary condition
                                  Exhibit I-Z  Page 9

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Tcn'.ative Rating Method for Samtary Landfill Operations
of the fill should be  maintained at all times
and for this reason a high score  must be
attained on certain items in order to assure
the proper degree of health protection.

A  suggested method of evaluating the numeri-
cal ratings is as follows:

A_-Rated Sanitary Landfill - Suitable for well-
developed areas  such as residential and
commercial zonings.

The following items must score as follows:

      Item 9   (Blowing Litter)       4

      Item 12 (Daily Cover)         15

      Item 13 (Intermediate Cover)  3

      Item 14 (Final Cover)          3

      Item 18 (Burning)             3

      Item 22 (Placement in         5
              Ground Water)

      Item 23 (Drainage of Surface   4
              Water)

Total rating must equal 85 or more points.

n-Rated Sanitary Landfill - Suitable for areas
of industrial  zonings.

The following items must score as follows:

      Item 9   (Blowing Litter)       2

      Item 12 (Daily Cover)         10

      Item 13 (Intermediate Cover)  1

      Item 14 (Final Cover)          3
      Item 18 (Burning)              3

      Item 22 (Placement in Ground  3
              Water)

      Item 23 (Drainage of Surface    4
              Water)

Total rating must equal 70 or more points.

C-Rated Sanitary Landfill - Suitable for re-
mote or rural areas (to be determined locally -
approximate  conditions, less than 500 persons
per square mile).

The  following items must rate as follows:

      Item 9   (Blowing Litter)        2

      Item 12 (Daily Cover)          10

      Item 13 (Intermediate  Cover)   1

      Item 14 (Final Cover)           3

      Item 18 (Burning)              3

      Item 22 (Placement in Ground  3
              Water)

      Item 23 (Drainage of Surface    4
              Water)

Total rating must equal 55 or more points.

The  closer a sanitary  landfill is to human
habitation, the more stringently the landfill
must adhere  to good practice.   In order to
satisfy public demands, the sanitary landfill
ratings have  been developed  to indicate the
quality of sanitation landfills must maintain
to operate in the three principle types of
areas.  In many  cases, sanitary landfills may
attain a rating appropriate for the area in
which they are located, through  modifications
to achieve adequate scores on certain items.
  10
                                Exhibit 1-2  Page 10

-------
EXHIBIT II  -1   ELM TREE STATISTICAL INFORMATION

I.     GENERAL
                    a.     Square Miles                               1,530
                    b.     Acres                                    997, 120

     _B.      Mean Tree Measurements (Average of Samples Surveyed)

             1.      Definitions

                    a.     100% Density - Total estimated material
                          with same density as the log or trunk.
                    b.     Wet Weight - Green  log or foliage material.
                    c.     Dry Weight - Oven-dried material, 0% moisture.

             2.      Average Diameter  - Inches                           23

             3.      Average Overall Height  - Feet                        25

             4.      Log or Bole (Limb Free Trunk) Volumes

                    a.     Length @ 50% of average overall  height-feet     12. 5
                    b.     Average diameter -  Inches                      23.
                    c.     Volume cubic feet (cubic yards)                 36 (1. 3)

             5.      Crown (upper foliage and limbs) absolute
                    volumes (equal to  bole)

                    a.     Volume Cubic Feet (Cubic Yards)               36 (1. 3)

             6.      Total Volume

                    a.     Cubic Feet (cubic yards)                        72 (2. 6)

             7.      Weights
                    a.     Pounds per cubic feet, wet                      54. 3
                    b.     Pounds per cubic feet, dry                      34
                    c.     Bole,  wet (54. 3 x 36) -pounds (tons)         1,955 ( .9?)
                    d.     Crown, wet  (54. 3 x 36) - pounds  (tons)      1,955 ( .97)
                    e.     Total tree, wet (54. 3 x 72) -pounds(tons)    3,910 (1.94)
                    f.     Total tree, dry (34 x 72)-pounds(tons)       2,448 (1. 2)
                    g.     Ash residue  (2. 2% of dry wt. )-pounds           54
                          Exhibit II-1,  Page 1

-------
      C.     Timberland (Acres)

             1.      Douglas County

                    a.    Private                                 53,416
                    b.    Public and semi-public                   9,247
  *                 c.    Parks and recreation                     3, 726
                                  Total                          66,389

             2.      Sarpy County

                    a.    Private                                 5,593
                    b.    Public and semi-public                  4,072
                    c.    Parks and Recreation                    1,572
                                  Total                         11,237

             3.      Pottawattamie County

                    a.    Private                                13,768
                    b.    Public and semi-public                  6, 545
                    c.    Parks and recreation                    2, 607
                                  Total                         22,920

             4.      Total SMSA Timberland - Acres             100,546

      D.     Average Acre Density (Estimated)

             1.      Private  - Per  acre                             2. 5
             2.      Public and  semi-public - per acre               5. 8
             3.      Parks and recreation - per acre                40. 0

II.    NUMBER OF ELM TREES (estimated)

      A.     Metropolitan Area

             1.      Douglas County

                    a.    Private                               133,540
                    b.    Public and semi-public                 53,633
                    c.    Parks and recreation                  149, 040
                                  Total                        336,213

             2.      Sarpy County

                    a.    Private                                13,983
                    b.    Public and semi-public                 23,618
                    c.    Parks and recreation                   62,880
                                  Total                        100,481


                          Exhibit II-1, Page 2

-------
3.      Pottawattamic County

       a.     Private                                  34,420
       b.     Public and Semi-public                    37,961
       c.     Parks and recreation                    104,280
                     Total                           176,661

4.      Metropolitan Area Disposal Problem Trees

       a.     Original Total elm, 100%                613,355
       b.     Down and disposed, 1964-1968,  35%      214,674
       c.     Remaining standing, 1968, 65%           398,681

5.      Total Metropolitan Area Disposal Problem
       Trees                                        398,681

6.      Number of Immediate and Rural Area
       Disposal Problem Trees.
       a.     Total Metropolitan Area Disposal
             Problem trees -                         398,681
       b.     Estimated continued on-site disposal
             of rural or remote areas, 23% of total -    91, 697
       c.     Total immediate area disposal problem
             trees -                                  306,984

7.      Total Metropolitan Area Elm  Tree Weight

       a.     Immediate area (1. 94 Tons x 306,984
             trees) - tons                             595,549
       b.     Rural or remote area (1. 94 tons x91,697
             trees) - tons                             177,892
       c.     Total - Tons                             773,441
             Exhibit II-1, Page 3

-------
           EXHIBIT II-2 -  DEVELOPMENT OF UNIT WEIGHTS

A.	GENERAL.  Unit weights are intended to be typical of materials
"As Delivered" to the disposal site, but often loads are mixed,  with two or
more materials in each load.  Seldom is there only one material on a load,
except in the case of certain material classes which are intended to include
a'variety of materials peculiar to the origin or type of waste.

It was often impractical to  define all components of a  load.  For instance,
a load of glass from a bottling  company also contained quantities of paper,
cardboard,  wood, tin cans, etc.  Therefore, loads were estimated as to the
percentage of major components, on a volumetric basis.

Weighing of waste as delivered to the site was done in order to obtain unit
weight data on materials for which there was no other information and to sub-
stantiate data available from other sources.  An attempt was made to select
loads for weighing which were typical for that class of material, although
some weighing of mixed loads  was required.   Mixed loads were analyzed on the
basis of component parts to check the total weight of the load against known
or assumed average weights of two or more components.

Many material densities were  assigned based upon specific knowledge of the
materials involved,  while others are a matter of general  knowledge.  Past
experience has provided knowledge of such items as paunch manure, sewage
solids,  street sweepings, rubber manufacturing wastes, cinders,  fly ash
and cement manufacturing wastes.  The bulk density of various materials are
general knowledge, including dirt, gravel rock, oils,  grain, fruits and vege-
tables,  furniture and appliances.

J3_.	WEIGHING PROGRAM.  Three approaches to weighing of refuse ma-
terials were taken. These are discussed in the following paragraphs.

          JU     City Collected Wastes - All domestic kitchen waste disposed
of at the Council Bluffs Landfill was  collected by the  City of Council  Bluffs in
packer trucks.  As a part of the refuse collection  study, a record  was made of
the  volume of refuse collected by the City of  Council  Bluffs packer trucks for at
le^lst one week on each of the  6 routes.  From this date, unit weights were de-
termined by weighing a number of loads and averaged to determine a unit -weight
for  material Class 40,  "Garbage and Kitchen Wastes, Domestic."  The average
density was 626 Ib/c. y. ,  with  a maximum of 750 Ib/c. y.  and a minimum of
500 Ib/c.y.   A value of 626 Ib/c.y. packed or 313 Ib/c.y.  loose was assigned to
material Class 40.  This value was also assigned  to material Class 41,  "Gar-
bage and Kitchen Wastes, Commercial. "

          2_.      Weighing  of Private Haulers - Private refuse haulers cooper-
ated in obtaining unit weight data for  several classes of material,  particularly
the  "paper and cardboard" and "mixed trash and refuse" classes.  There is
considerable variation in the unit weight of these wastes depending upon whether


                          Exhibit II-2,Page 1

-------
they are collected in packer trucks,  open body trucks, trailers, or pickups.
Numerous loads of both packer and non-packer type trucks were weighed and
recorded the corresponding volumes.

For material Class 42,  "Mixed Trash and Refuse (including Garbage), " weigh-
ing of packer and open body trucks produced the following results:
                                                                             r
                  No.  of Loads   Volume      Weight          Ave.Unit Weight

Open Truck           35            241 CY      74,310 Ibs.       3081b/c.y.
Packer  Truck        357         5,9HCY  3,650, 310 Ibs.       6l71b/c.y.

The unit weight assigned to material Class 42 "Mixed Trash and Refuse (inclu-
ding Garbage)" was 308 Ib/c.y. for open body trucks and 6l6 Ib/c.y. for packer
trucks.

For material Class 43,  ''Mixed Trash and Refuse (No Garbage), " weighing of
packer and open body trucks produced the following results:

                  No. of Loads   Volume       Weight         Ave. Unit Weight

Open Truck           84            716 CY    166, 710 Ibs.       231 Ib/c.y.
Packer  Truck         75         1.200CY    564, 000 Ibs.       470 Ib/c.y.

The unit weight assigned to material Class 43, "Mixed Trash and Refuse (No
Garbage)" was 232 Ib/c.y. for open body trucks and 464 Ib/c.y. for packer
trucks.

For Material Class 50,  "Paper and Cardboard, " weighing of packer and open
body trucks produced the following results:

                 No. of Loads    Volume       Weight         Ave. Unit Weight

Open Truck           91            965 CY    178,160 Ibs.       183 Ib/c.y.
Packer  Truck         24            384 CY    138, 240 Ibs.       360 Ib/c.y.

The unit weight assigned to material Class 50, "Paper and Cardboard, " was
185 Ib/c.y.  for open body trucks  and 370 Ib/c.y. for packer trucks.

The 2 to 1 compaction ratio of packer trucks to open trucks established in ma-
terial classes 40,  41, 42,  43 and 50  is believed to hold true for each of these ma-
terial classes.  On that basis,  open truck unit weights of 313 Ib/c.y. were as-
signed to material Classes 40 and 41, 308 Ib/c.y.  for material class 42,  232 lb/
c.y. for material  Class 43, and 185  Ib/c.y. for material Class 50.
                          Exhibit II-2, Page 2

-------
          _3.      Packer Truck Density - For the five material Classes 40,
41, 42, 43 and 50, the 2 to 1  compaction ratio of packer to open truck density
was incorporated into the computer program for determining the weight of
material delivered to the disposal site.  Unit weights listed in the table giving
seasonal and compact]on factors and unit weights are fdr open trucks.  When
these material classes were delivered in packer trucks, both the unit weight
and the compaction factor were automatically doubled.  This eliminated the
need for anticipating the ratio of packer trucks to open trucks in each material
class and permitted the use of two unit weights for these materials rather than
a single weighted average based on an anticipated ratio of truck type.

          _4.      Random Weighing.  The third approach to load weighing was
random weighing of typical loads observed at the landfill sites.  This was used
exclusively for the demolition and tree  waste categories, and also for other
materials.
                                            /
_C.	COMPACTION FACTORS.  Compaction factors were determined,
based upon the anticipated density of the material in  the fill as  compared to
the density as delivered to  the disposal site.  For instance, paper, cardboard,
and general mixed rubbish  should compact in the fill to approximately 600 lb/
C. Y.   If paper and cardboard are delivered to the disposal site in an open body
truck at 185 Ib/C. Y. , the compaction factor is determined to be  1854600 =  0. 3,
If (he same  material is delivered in a packer truck at 370 Ib/C. Y. , the com-
paction factor is 3704600 -  0. 6.  Some  materials will have a greater  density
delivered to the site  than the compacted density of paper and other rubbish.   In
the case of liquids and semi-solids, little or no increase in the fill volume may
be  required, therefore a small compaction factor is  used.  Heavy granular and
bulky wastes were evaluated in terms of the anticipated volume reduction due to
spreading, compacting and mixing with other materials in the landfill for assign-
ing compaction compaction  factors.
                          Exhibit. IJ-2,  Page 3

-------
EXHIBIT  :nr - i
Page I
                        SITE  SIMULATION  NO.  65
SlMULiTIO^ NUM-tFrf
SITE 1 DISPOSAL F
MINJMUH FE

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                                Exhibit III-l, Page 1

-------
EXHIBIT m- I
Page 2
if." 1CLE 01STR1HUTION "Y  DISPOStL  SITES
                                    SITE  SIMULATION  NO.  65
                                                            _ VFHICLF PTSTRlRtlTIfK- PY HISPOSflL  SITES.
                                                                    VEHICLE     PC0  NO. OF   CU«IC     TON5
                                                            	TYPE	_flQEfl  VEHICLES rflPOj^	
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26 38
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                                              Exhibit III- 1,  Page 2

-------
EXHIBIT  HI - 2
Page I
                        SITE  SIMULATION NO. 87
,,,r , -MSPOS.L F" l.?<

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                               Exhibijt HI-2,  Page  1

-------
EXHIBIT m - 2 SITE SIMULATION NO. 87
Pog« 2
VEHICLE DISTRIBUTION RY OJSPOSAL SITES VEHICLE DISTBIHUTinM qy
vFH/ei_e GeQ M. OF CU9JC TONS

SITE 3 i
3 ? 7
V 2 12
IS 71 112
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Exhibit III-2,  Page Z

-------
EXHIBIT 3JT- 3
Page I
                         SITE SIMULATION  NO. 92
s
7TF 3 DISPOSAL f £ 1 ,?*>
,,,,„



TS6NSFES F F n.OO/TD'J
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TOTALS row ALL V^ICLES
SITF CU YOS TfiNS
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                               Exhibit III-3, Page 1

-------
 EXHIBIT m - 3
 Paje 2
                                  SITE  SIMULATION  NO. 92
                            SITFS
                             mm
                                             tVf&AKt
                                              FFl-S
                                                         VEHICLE niSTHlBUTIOM BY llSPOSaL SITES
                                                                         G£iT ^JT. ~OF"
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                                            Exhibit III-3,  Page  2

-------
                  EXHIBIT III - 4
COST ESTIMATE - SOLID WASTE DISPOSAL FACILITIES
       SANITARY LANDFIU. SITES 3, 5, and 7
BASIC COST DATA
1.
2.
3.
4.
5.
6.
7.
8.
9.
Land Cost
N.W. Site (3) 240 Acres @$ 1200
S.E. Site (5) 480 Acres® $1000
N.E. Site (7) 160 Acres @$ 1000
Initial Site Development
N.W. Site (3)
S.E. Site (5)
N.E. Site (7)
Annual Maintenance & Site Development
N.W. Site (3)
S.E. Site (5)
N.E. Site (7)
Equipment Purchase
/A = $288, 000
/A = 480,000
/A= 160,000
$129,500
162,500
112,000
$ 25,000
30,000
15,000

Cost of New Equipment, One Time Purchase Only
Equipment Maintenance, Operation, and Amortization
Item Hrs/Yr,
Track Loader 2496
Track Loader 3744
Track Looder 2496
Compacter 2496
Dozer 2496
Dozer 2496
Grader 2080
Water Trucks 2496
Tractor/Mower 1040
Lowboy Trailer (100)
Dump Truck (100)
Pickup Trucks
Miscellaneous
Dozer (Spare) (200)
Wheel Loader (Spore) (200)
Total 22,440
Labor Hrs/Yr.
Equip. Operators 21,840
Laborers 15,184
Foremen 7,488
Gatekeepers 11,232
Headquarters & Maintenance Building
Office and Maintenance Building
Office and Maintenance Equipment
Agency Operation
Salaries
Overhead
Miscellaneous Expense & Contingencies
Rate/Hr. Cost/Yr.
$10.00 $25,000
15.00 56,200
7.00 17,500
19.00 47,400
11.00 27,500
9.00 22,500
5.50 11,400
4.00 10,000
2.00 2,100
3.00 300
5.00 500
3,000
8,400
9.00 1,800
7.00 1,400
Rate/Hr. Cos,Ar.
$ 4.25 $92,800
3.25 49,400
4.75 35,600
3.75 42,100
$80,000
50,000
$51,000
14,000

$928,000
$404,000
$ 70,000
$462,000
$235,000
$219,900
$130,000
$ 65,000
$ 60,000
                Exhibit 111-4, Page 1

-------
 ANNUAL COST
        One-Ttme Expense
            (erf - 6% - 20 Yr. = 0.08718)
        Land Cost
        Initial  Site Development
        Equipment Purchase
        Hdqtrs   Building
        Reoccuring Annual Expense
        Stfe Maintenance & Development
        Equip  M.O  & A
        Labor
        Agency Operation
        Misc. & Contingency
 3.     Total Annual Cost

 FIXED &  VARIABLE ANNUAL COSTS
                 $ 928,000
                   404,000
                   462,000
                   130,000
                 1,924,000
                  $ 70,000
                   235,000
                   219,900
                    65,000
                    60,OOP
                                                                           $167,700
                                                                           S649,900

                                                                           5817,600
       Debt Expense                   $ )67;700
       Annual Development
       Equip. M. O. & A.               11,400
       Labor                          127,100
       Agency Operation                65,000
       Misc  & Contingency                ~
                                     $371,200

QUANTITIES FOR UNIT AND TOTAL COSTS
                   Variable Costs

                 t  70,000
                   223,600
                    92,800

                    60,000
                 $446,400
       IstYr.,  1970
       4th Yr.,  1973
Ac-Ft.
  604
  559
UNIT AND TOTAL COST OF OPERATION
Tons
7237000
666,000
 1.     IstYr.  1970  604 Ac.-Ft.  723,000 Tons
       Fixed  Cost       $371,200  -  604 As.  Ft. =
       Variable         {446,400  T  604 Ac.  Ft. =
       Total           $817,600

       $817,600r  723,000 Tons =$1.13/Ton

2.     4th Yr.  1973  559 Ac-Ft.  666,000 Tons
       Fixed Cost
       Variable Cost  559 Ac-Ft. x 740/Ac-Ft.

       $784,900 - 559 Ac-Ft. =          $l,405/Ac-Ft.
       $784,900 - 666,000 Tons =        $ 1.18/Ton

BOND DEBT SERVICE  RESERVE
                  $615/>c-Ft.
                  $740/Ac-Ft.
                  $371,200
                   413,700
           0.4(167,700) =$67,100
1.     IstYr.  1970567,100-  723,000 Tons =
2.     4th Yr.  1973 $67, 100 -666,000 Tons =

SUMMARY OF UNIT COSTS
                 Operation
       _
       TW     rrn
       1973       $1.18
                  $  0.09Aon
                  $  O.)0/Ton
                  Total
                  Unit Cost
                  S/T°"
                       —
                                                        $1.28
                                Exh.bir 111-4, Page 2

-------
INDIVIDUAL SITE DATA

1.      Refuse Accumulation and Land Requirements
       1970 -  1st Year of Operation
                 Ac-Ft.*     Fill DeptK       Fill Are
       Site 3     «W~      3B1             20?
       Site 5     9730        24'             405
       Site 7     3300        24'             138
                 * Compacted and Seasonally Adjusted
2.     Tom of Refuse Pet Day, 1970/1995
                 Operation,  pjys/Week
       Site 3              6
       Site 5              6
       Site 7              6
                 ** Seasonally Adjusted

3.     Initial Site Development and Costs

       Scale House, Equip. Bldg.
          & Pers. Facilities (3)
       Scales (5)
       Scale Equipment (3)
       Watermain 7000'
       Perimeter Fence 48,000'
       Entr. Fence 3,000'
       Gravel Surf.
       Grading
       Landscaping
       Yard Lighting
       Apron Pum't
       Miscellaneous
       Total

4.     Equipment Cost and Distribution

       Item
       3 Track Loaders
       1 Compactor
       2 Dozers
       1 Grader
       2 Water Trucks
       1 Tractor/Mower
       3 Pickup  T.ucks
       1 Lowboy Trailer
       1 Dump Truck
     '  Miscellaneous
       1 Dozer  (Spare)
       1 Wheel Loader (Spare)
       Total Equipment Cost

5.     Equipment Hours Per Year
       Track Loader,  170 FWHP
       Track Loader,  275 FWHP
       Track Loader,  115 FWHP
       Compacter,    400 FWHP
       Dozer,        180 FWHP
       Dozer,        125 FWHP
       Grader,       125 FWHP
       Water Trucks
       Tractor/Mower
       Lowboy Trailer
       Dump Truck
          Spare Equipment
       Dozer,        125 FWHP
       WKeel  Loader, 130 FWHP
               xl.2
               24T
               487
               165
            240A
            4BOA
            160A
Tons Per Da)
700/1260
1200/1750
410/590
Site 3
$30,000
18,000
10,000
10,000
7,500
2,000
5,000
18,000
9,000
4,000
10,000
6,000
$127,500
Site 3
$467500
-
$50,000
7,500
4,000
600
4,000
2,000
3,500
2,500
10,000
12,000
$142,100
/**



SiteS
$30,000
18,000
10,000
15,000
10,000
2,000
10,000
30,000
12,500
5,000
10,000
10,000
$162,500
SiteS
$767000
74,000
-
12,500
8,000
1,000
4,000
3,500
6,000
4,000
18,000
21,000
$222,000




Site 7
$30,000
9,000
10,000
10,000
6,500
2,000
4,000
15,000
8,000
3,500
10,000
4,000
$112,000
Site 7
sJeTooo
-
35,000
5,000
4,000
400
4,000
1,500
2,500
1,500
7,000
9,000
$$97555
$462,000
Site 3
2,496
-
-
2,496
-
6^0
748
320
(30)
(30)
(60)
(60)
6,880
Site 5
3,744
-
2,496
-
_
1,040
1,248
520
(50)
(SO)
(100)
(100)
'97545
Site 7
~
2,496
-
-
2,496
400
500
200
(20)
(20)
(40)
(40)
6,212
6.     Annual Equipment Operator Hours
                                             6,700
                                                         9,048
                                                                      6,092
       Labor Hours Per Year
       Type
       Equip. Operator
       Labore rs

       Gatekeepers
Site 3
6,700
4,160
2,496
3,744
Sue 5
'97048
8,320
2,496
3,744
Site 7
67592
2,704
2,496
3,744
Total
7T7840
 15,184
 7,488
 11,232
                                  Exhibit 111-4, Page 3

-------
                                   EXHIBIT III - 5
                 COST ESTIMATE - SOLID WASTE DISPOSAL FACILITIES
                          SANITARY LANDFILL SITES 3 ond 5

BASIC COST DATA

1 .     Land Costs

       N.W. Site (3)     400A 'a- 1200/A = $480,000
       S.E.Site(S)      _520A'cc 1000/A =  520,000
                         920 Acres                                          $1,000,000

2.     Initial Site Development (2 sites)

       Scale House        2430,000=   $60,000
       Scales             4 U  9,000=   36,000
       Scale Equipment    2 S 10,000 =   20,000
       Equipment Bldg.
       &Pers. Facilities   2930,000=   60,000
       Watermam 8" x 6000'             30,000
       Per,m. Fence 35,000'              18,000
       Entr. Fence 2,000'                  4,000
       Gravel Surfacing                 30,000
       Grading                          60,000
       Landscaping                      25,000
       Yard Lighting                     10,000
       Apron Pavement                   10,000
       Miscellaneous                     17,000                            $  380,000

3.     Annual Maintenance & Site Development Cg- $30,000 each                $   60,000

4      Equipment Purchase

       Cost of New  Equipment, One Time  Purchase Only                       $  443,000

5.     Equipment Maintenance, Operation, and Amortization

2 - Track Loaders,
275FWHP
2 - Compactors,
400FWHP
1 - Grade,, 125FWHP
2 - Water Trucks
1 - Tractor Mower
2 - Pickup Trucks
1 - Lowboy Trailer
1 - Dump Truck
M scellaneojs
1 - Dozer,
125FWHP(Spaiel
1 - Wheel Loader,
130FWHP (Spare)

Laboi

Equipmf-n' Operators
Laborer' -"/Site
Foreman, l.'jite
Gatekeepei
Hrs./Y'.

7488

4992
2080
2496
1040
—
(100)
(100)
__

(200)

(200)
T8,696

Mrs .A'.
18,096
16,640
4,992
7,488
Rate/Mr.

$15.00

19.00
5.50
4.00
2.00
—
3.00
5.00
—

9.00

7 00


Rote/Hr.
$ 4.25
3.25
4.75
3.75
CostA' •

$112,300

95,000
11,400
10,000
2,100
2,000
300
500
5,200

1,800

1,400
$ 242,000

CostAr.
$76,900
54,100
23,700
28,100
                                                                         $  182,800

      Headquarteis & Maintenance Building

      Office and Moii.tenance Bldg             $80,000
      Office and Ma,n'enance Equip             50,000                     $  130,000

      Agency Operation'

      Salaries                                $51,000
      Overhead                               14,000
                                                                         $   65,000

      Agency Misc.  Expense & Contingencies                                $   60,000
                                        11-5, Page 1

-------
ANNUAL COSTS
1.



2.




One-Time Expense (CRF-6%-20Yr. =

Land Cost
Initial Site Development
Equipment Purchase
Hdqts. Bldg.
.08718
Reoccurring Annual Expense
Site Maintenance & Development
Equipment M.O. & A.
Labor
Agency Operation
Misc. & Contingency
0.08718)
$1,000,000
380,000
443,000
130,000


$ 60,000
242,000
182,800
65 000
60,000

3.     Total Annual Costs

FIXED & VARIABLE ANNUAL COSTS
  Debt Expense
  Annual Development      —
  Equipment M.O. & A.    7,200
  Labor                 105,900
  Agency Operation       65,000
  Misc. & Contingency     —
                       $348,400
                            Fixed Costs   Variable Costs
                           $170,000
QUANTITIES FOR UNIT AND TOTAL COSTS


       1st Yr.  1970
  .
2.     4th Yr. 1973
3.     Avg. Yr. 1982
4.     FinalYr. 1995
                        Ac . Ft .
                          604
                          559
                          718
                          949
                                            $60,000
                                            234,800
                                              76,900

                                              60,000
                                            $431,765"
                                             Tons
                                             7537553"
                                             666,000
                                             853,000
                                            1,124,000
  UNIT AND TOTAL COSTS OF OPERATION

  1.     1st Yr. 1970  604 Ac. Ft.  723, 000 Tons
         Fixed Cost $348,400 ?  604 Ac/Ft. =     $575/Ac-Ft.
         Variable Cost $431,700-; 604 Ac/Ft. =    7|5/Ac-FK
                     $780,1000              $T,2907Ac-Ft.
         $780,100 - 723,000 Tons = $l,08/Ton

         4th Yr. 1973 559 Ac. Ft.  666,000 Tons

         Fixed Cost                            $348,400
         Variable Cost
               559-Ac-Ft. x $715/Ac-Ft.  =       399,700

         $748,100 r 559 Ac.  Ft. =$l,340/Ac. Ft.
         $748,100 r 666,000 Tons = $1.12A°n

          Avg.Yr.  1982 718  Ac. Ft. 853,OOOTons

          Fixed Cost                           $348,400
          Variable Cost
               718 Ac-Ft. x  $715/Ac-Ft          513,400
                                               $86i7§o3
          $861,800 r 718 Ac-Ft. = $1,200 Ac-Ft.
          $861,800 r 853,000 Tons = $1 .OlAon

          Final Year 1995 949 Ac. Ft.  1,124,000 Tons

           Fixed Cost                            $348,400
           Variable Cost
                949 Ac-Ft x $715/Ac-Ft.          '™ *""
                                        $1,026,900

      $1,026,900 r 949 Ac-Ft. = $l,080/Ac.  Ft.
      $1,026,900 r l,124,000 = $0.92/Ton

BOND DEBT SERVICE RESERVE

      0.4 (170,300) = $68,100

       1.   1st Yr. 1970    $68,100 r    723,OOOTor,s
       2.   4th Yr. 1973     68,100 r    666,000 Tons
       3.   Avg.Yr. 1982   68,100 r    853,OOOTons
       4.   Final  Yr. 1995   68,100 r   1,124,000 Tons
      SUMMARY OF UNIT COSTS
            Year
            T970
             1973
             1982
             1995
                                                                       $  170,000
                                                                       $  609,800

                                                                       $  780,100
                                                                  $0.10A°n
                                                                  $0.10/Ton
                                                                  $0.08Aon
                                                                  $0.06Aon
                                       Exhibit IU-5, Poge 2

-------
INDIVIDUAL SITE DATA
        Refuse Accumulation & Land Requirements
        1970  1st Year of Operation
               Ac-Ft.*       Fill Depth        Fill Area
        Site 3  9380          W              313 Ac'
        Site 5  9830          24'              410 Ac
        Totals  13,210
               'Compacted and Seasonally Adjusted

        Tons of Refuse Per Day, 1970/1995

        Site    Operation, Pays/Week
        3               6
        5               6
               ** Seasonally Adjusted

        Equipment Cost and Distribution

        Item                                  Site 3
        2  Track Loaders, 275 FWHP           $70,000
        2  Compactors, 400 FWHP               74,000
        1  Grader, 125 FWHP                  12,500
        2  Water Trucks                        8,000
        I  Tractor/Mower                       1,000
        2  Pickup Trucks                       4,000
        1  Lowboy Trailer                      3,500
        I  Dump Truck                         6,000
        Miscellaneous                         4,000
        1  Dozer, 125FWHP (Spore)              17,500
        1  Wheel Loader, 130FWHP (Spore)     21,000
                                          5221,500
   Purchase Area
Total Equipment Cost
Equipment Hours Per Year
Item
Track Loader, 275FWHP
Compactor, 4QOFWHP
Grader, I25FWHP
Water Truck
Tractor/Mower
Trailer
Durnp Truck
Dozer, I25FWHP (Spare)
Wheel Loader, I30FWHP (Spare)



Site 3
374T-
2496
1040
1248
520
( 50)
( 50)
( 100)
( 100)
9W
       Annual Equipment Operator Hours
       9048 Hours Each Site

       Labor Hours Per Year

       Type                                 Site 3
       £quip. Operators                      9,098
       Laborers, 4/5ite                       8,320
       Foreman                              2,496
       Gatekeeper                           3,744
  Site 5
  74,000
  12,500
   8,000
   1,000
   4,000
   3,500
   6, 000
   4,000
  17,500
  21,000
J22OOO
                                                          $443,000
                                                                     SiteS
                                                                     373T"
                                                                     2496
                                                                     1040
                                                                     1248
                                                                      520
                                                                    (  50)
                                                                    (  50)
                                                                    ( 100)
                                                                    ( 100)
                                                                     934T
 Site 5
 8,320
 2,496
 3,744
 Total
187T96
16,640
 4,992
 7,488
                              Exhibit 111-5, Page 3

-------
                             EXHIBIT III - 6
                 COST ESTIMATE - SOLID WASTE DISPOSAL FACILITIES
                         SANITARY LANDFILL SITES 3, 5, ond 7
BASIC COST DATA
                                  80 A @ 1,200.00/A =
                                 320 A @ 1,200.00/A =
                                 480 A @ 1,000.00/A =
       Land Cost
            S.W. Site  (1)
            N.W. Site (3)
            S.E. Site   (5)
2.     Initial Site Development

            S.W. Site  (1)
            N.W. Site (3)
            S.E. Site   (5)

3.     Annual Maintenance & Site Development

            S.W. Site  (1)
            N.W. Site (3)
            S.E. Site   (5)

4.     Equipment Purchase

            Cost of New Equipment, One Time Purchase Only.

5.     Equipment Maintenance, Operation, and Amortization
Item
Track Loader
Track Loaders
Compactors
Grader
Water Trucks
Tractor/Mower
Lowboy Trailer
Dump Truck
Pickup Trucks
Miscellaneous
Dozer (Spare)
Wheel Loader (Spare)
Hrs/Yr.
2,080
7,488
4,992
2,080
2,496
1,040
(100)
(100)
-
-
(200)
POO)
Rote/Hr.
JI8.63
15.00
19.00
5.50
4.00
2.00
3.00
5.00
-
-
9.00
7.00
Cost/Yr.
( 20,800
112,300
94,800
11,400
10,000
2,100
300
500
3,000
8,400
1,800
1,400
                                                                           $960,000






                                                                           (362,500





                                                                           $ 65,000


                                                                           $494,000
                                                                           $266,800

Item
Equip. Operators
Laborers
Foremen
Gatekeepers
Hrs/Yr.
Total
20, 176
14,560
4,992
V,568

Rate/Hr.
PT53
3.25
4.75
3.75

Cost/Yr.
iS.TWT"'
47,300
23,700
35,900
7.     System Hoqtrs. & Maintenance Bldg.

       Office 4 Maint. Bldg.      $80,000
       Office 4 Maint. Equip.       50,000
       Agency Operatiot

       Salaries
       OverSead
                                $51,000
                                 14,000
9.     Miscellaneous Expense & Contingency
                                                                           $192,600
                                                                           $130,000
                                                                          $  65,000

                                                                          $  60,000
                                Exhibit 111-6, Page 1

-------
 ANNUAL COST DATA
       One-Time Expense    (crf-i
       Land Cost
       Initial  Site Development
       Equipment Purchase
       Hdqtrs. Bldg.
                                 ,-20 Yr. =0.08718)
                                       $960,000
                                        362,500
                                        494,000
                                        130,000
                                     $1,946,500
                                                                          $163,700
       Operating Expense

       Site Mainr & Development
       Equip. M.O. & A
       Labor
       Agency Operation
       Misc. & Contingency
3.     Total Annual Cost

FIXED AND VARIABLE ANNUAL COSTS
                                       $ 65,000
                                        266,800
                                        192,600
                                         65,000
                                         60,000
Debt Expense
Annual Development
Equip. M. O. & A.
Labor
Agency Operation
Misc. & Contingency
Fixed Costs
11,400
106,900
65,000
$353,666
Variable Costs
$ 65,006
255,406
85,760
66,666
$466, 100
                                                                          $649,400

                                                                          $819,100
QUANTITIES  FOR UNIT AND TOTAL COSTS
1st Yr.
4th Yr
., 1970
., 1973
Ac. -Ft.
604 	
559
Tons
7537606
666,600
UNIT AND TOTAL COST OF OPERATION
       IstYr. 1970  604 Ac.  Ft.  723,000 Tons
       Fixed  Cost      $353,000 -  604 Ac. Ft. =
       Variable Cost    466,100 -  604 Ac. Ft. =
                      $819,100

       S819,100 -  723,000 Tons = $1.13/Ton

       4th Yr., 1973 559 Ac. Ft.  666,000 Tons
       Fixed Cost
       Variable Cost 559 Ac.  Ft. x $770/Ac. Ft. =
                                       $585/Ac. Ft.
                                       $770/Ac. Ft.
                                     $l73557Ac. Ft.
                                       $353,600
                                        430,406
                                       $783,460
       $783,400- 559 Ac. Ft.  =
       $783,466 - 666,000 Tons =
BOND DEBT SERVICE RESERVE
                       $l,400/Ac. Ft.
                       $I.18/Ton
            0.4 (169,700)
1.     IstYr.,  1970     $67,900- 723,000 Tons =
2.     4th Yr ,  1973     $67,900 - 666,000 Tons =

SUMMARY OF UNIT COSTS
Operation Cost
      T^TO      $1  13
       1973      $1.18
                                       $0.11
                                       $6.10/Ton
                                       $0.1 lAon
                                                        Total
                                                        Unit Cost
                                                        $A°"
                                                        $1.29
                                  Exhibit 111-6, Page 2

-------
INDIVIDUAL SITE DATA
       Refuse Accumulation and Land Requirements
       1970- 1st Year of Operation
                 Ac.-Ft.     Fill Depth
       Site 1     1800        30'
       Site 3     7630        30'
       Site 5     9780        24'
       Totals     19,210

       Tons of Refuse per Day, 1970/1995
                 Operation,  Days/Week
       Site I              5
       Site 3              6
       Site 5              6

       Initial Site Development and Costs

       Scale House,  Equip. Bldg.
         & Pers.  Facilities
       Scales
       Scale Equip.
       Wotermam 7000'
       Perim. Fence  42,000'
       Entr. Fence 3,000'
       Gravel
       Grading
       Landscaping
       Yard Lighting
       Apron Pavement
       Miscellaneous
       Equipment Cost and  Distribution
       Item
       3 Track Loaders
       2 Compacters
       1 Grader
       2 Water Trucks
       1 Tractor/Mower
       3 Pickup Trucks
       I Lowboy Trailer
       1 Dump Truck
       Miscellaneous
       J Dozer (Spare)
       1 Wheel Loader (Spare)
       Total  Equipment Cost

5.     Equipment Hours per Year
       Track Loader,  170FWHP
       Track Loader,  275FWHP
       Track Loader,  275FWHP
       Compacters, 400FWHP
       Grader,  120FWHP
       Water Trucks
       Tractor/Mower
       Lowboy Trailer
       Dump Truck
       Dozer,  125 FWHF (Spare)
       Wheel  Loader,  130FWHF (Spare)
       Annual Operator Hours
       Labor Hours per Yeai

       Equip. Operator
       Laborers
       Foremen
       Gatekeepers
Fill Area
60 Ac.
254 Ac.
407 Ac.

Tons Per Da
220/480
920/1440
1210/1760
Site 1
520,000
--
—
10,000
3,500
2,000
2,000
8,000
6,000
2,000
10,000
3,000
566,500
Site 1
546,000
--
2,500
1,500
200
4,000
1,000
1,000
800
3,400
5,000
$65,400
5494, (XX
Site 1
2,080
—
—
—
240
248
120
(10)
(10)
(20)
(20)
2,748
2,688
Site 1
2,688
—
—
2,080
xl.2
72 Ac.
305 Ac.
489 Ac.

y



Site 3
530,000
18,000
10,000
10,000
7,500
2,000
6,000
20,000
10,000
4,000
10,000
6,000
5133,500
Site 3
S70TOOO
74,000
10,000
6,500
800
4,000
2,500
5,000
3,200
14,600
16,000
$206,600
)
Site 3
—
3,744
—
2,496
800
1,000
400
(40)
(40)
(80)
(80)
8,680
8,440
Site 3
8,440
6,240
2,406
3,744
80 Ac.
320 Ac.
480 Ac.
880 Ac




Site 5
530,000
18,000
10,000
15,000
10,000
2,000
10,000
30,000
12,500
5,000
10,000
10,000
$162,500
Site 5
sToTooo
74,000
12,500
8,000
1,000
4,000
3,500
6,000
4,000
18,000
21,000
$222,000

Site 5
—
—
3,744
2,496
1,040
1,248
520
(50)
(50)
(100)
(100)
9,348
9,048
Site 5
9,048
8,320
2,406
3,744
















































20,776
20,176
Total
207\76
14,560
4,992
9,568
                                 Exhibit MI-6, Poge 3

-------
                  EXHIBIT III - 7
COST ESTIMATE - SOLID WASTE DISPOSAL FACILITIES
      SANITARY LANDFILL SITES I, 3, 5, and 7
BASIC COST DATA
1.
2.
3.
4.
5.
6.
7.
Land Costs
S.W. Site(l)
N.W. Site (3)
S.E. Site (5)
N.E. Site (7)
Initial Site Develops
S.W. Site (1)
N.W. Site (3)
S.E. Site (5)
N.E. Site (7)
Annual Maintenance
S.W. Site (1)
N.W. Site (3)
S.E. Site (5)
N.E. Site (7)
Equipment Purchase,
80 Ac.@$l200//
200 Ac. @ 1200//
480 Ac. •S) 1000//
160 Ac. (a- 1000//
920 Ac.
lent
and Site Development

\c. = $ 96,000
Vc. = 240,000
Vc. = 480,000
\c. = 160,000
$ 66,500
122,000
162,000
112,000
$ 10,000
20,000
30,000
20,000
One-Time Purchase Only
Equipment Maintenance, Operation & Atnort
Item
Track Loader
Track Loader
Dozers
Scrapers
Compactor
Grader
Water Trucks
Tractor Mower
Trailer
Dump Truck
Pickup Trucks
Miscellaneous
Dozer (Spare
Wheel Loader (Spare)
Labor
Jj/pe
Equip. Operators
Laborers
Foremen
Gatekeepers
Headquarters and Mai
HrsAt .
2,080
2,456
7,488
(2,496)
2,496
2,496
2,406
1,248
(100)
(200)
(200)
(200)
20,800
Hrs/\r.
20,800
16,640
7,488
13,312
ntenance Bldg .
Office & Maintenance Building
Office & Maintenance Equipment
8. Agency Operation
9
Salaries
Overhead
Miscellaneous Expense and Contingencies
ization
Rate/Hr. Cost/Yr-
$10.00 $20,000
15.00 37,400
9.00 67,400
3.00 7,500
19.00 47,400
5.50 14,800
4.00 10,000
2.00 2,500
3.00 300
5.00 1,000
4,000
11,000
9.00 1,800
7.00 1,400
Rate/Hr. Cost/Yt .
$ 4.25 $88,400
3.25 54,100
4.75 35,600
3.75 49,900
$80,000
50,000
$51,000
14,000

$976,000
$453,000
$ 80,000
$475,000
$227,300
$228,000
$130,000
$ 65,000
$ 60,000
               Exhibit 111-7, Page 1

-------
ANNUAL COST DATA

1.     One-Time Expense
           (crf-6%-20 Yr. =0.98718)
       Land Cost
       Initial Site Development
       Equipment Purchase
       Headquarters Bldg.
                                       .08718
                                       $97d,000
                                        453,000
                                        475,000
                                        130,000
                                     $2,034,000
                                                                         5177,300
       Reoccurrmg Annual Expense

       Site Maint. & Development
       Equip. M.O. 8. A.
       Labor
       Agency Operation
       Misc. & Contingency
3.     Total Annual Cost

FIXED AND VARIABLE ANNUAL COSTS
                                       $  80,000
                                       277,300
                                       228,000
                                         65,000
                                         60,000

Debt Expense
Annual Development
Equip. M.O. & A,
Labor
System Operation
MISC. & Contingency
Fixed Costs
$ J77,300
—
18,200
139,600
65,000
— 	
Variable Costs
—
$ 80,000
209,100
88,400
—
60,000
                                                                         $660,300

                                                                         5837,600
                                                        $437,500
QUANTITIES FOR UNIT AND TOTAL COSTS
       1st Yr.,  1970
       4th Yr., 1973
                       Ac.-Ft.
                       604	
                       559
UNIT AND TOTAL COSTS

       lstYr.,1970     604Ac.Ft.    723,OOOTons
       Fixed Cost      $400,100 - 604 Ac.Ft. =
       Variable Cost     437,500 - 604 Ac. Ft.  =
                      $837,600

       4th Yr., 1973     559Ac.Ft.    666,000 Tons
       Fixed Cost
       Variable Cost     559 Ac.Ft.  X $725/Ac.Ft.
       $805,400 r  559 Ac. Ft. =         $ 1,440/Ao. Ft.
       $805,400 -  666,000 Tons =        $1.21/Ton

BOND DEBT SERVICE RESERVE
                                       $400,100
                                        405,300
                                       $805,400
       0.40 ($177,300)
       IstYr.,  1970     $71,000 - 723,000 Tons =
       4th Yr., 1973     $71,000 - 666,000 Tons =

SUMMARY OF UNIT COSTS
       Year
       1970
       1973
Operation Cost
  $/Ton
    $1.16
      1.21
                                        $0.10Aon
                                        $0.1 >A°n
Total
Unit Cost
$/Ton
$1.26
 1.32
                                 Exhibit 111-7, Page 2

-------
INDIVIDUAL SITE DATA
1,





Refuse Accumulation and Land Requirements
1970 - 1st Yr. of Operation
Ac. -Ft.* Fill Depth Fill Area xl.2 Purchase Area
Site 1 TS55 351
Site 3 4350 30'
Site 5 9770 24'
Site 7 3290 24'
Totals 19,210
60 Ac. 72 Ac. 80 Ac.
145 Ac. 174 Ac. 200 Ac.
407 Ac. 489 Ac. 480 Ac.
137 Ac. 165 Ac. 160 Ac.
920 Ac .





'Compacted and Seasonal!/ Adjusted
2.






3.














Tom of Refuse Per Day, 1970/1995
Operation, Days/Week
Site 1 5
Site 3 6
Site 5 6
Site 7 6
"Seasonally Adjusted
Initial Site Development and Costs
Item
Scale House, Equip. Bldg.
& Pers. Facilities
Scales
Scale Equip.
Watermain
Perim. Fence
Entr, Fence
Gravel Surfacing
Gradmg
Landscaping
Area Lighting
Apron Pavement
Miscellaneous

Tons Per Day**
220/480
510/850
1210/1750
410/580


Site 1 Site 3 Site 5

$20,000 $30,000 $30,000
9,000 18,000
10,000 10,000
10,000 10,000 15,000
3,500 6,500 10,000
2,000 2,000 2,000
2,000 4,000 10,000
8,000 15,000 30,000
6,000 ' 8,000 12,500
2,000 3,500 5,000
10,000 10,000 10,000'
3,000 4,000 10,000








Site 7

$30,000
9,000
10,000
10,000
6,500
2,000
4,000
15,000
8,000
3,500
10,000
4,000
$66,500 $112,000 $162,500 $112,000
4.















5.













6.

7.




Equipment Cost and Distribution
Item
2 Track Loaders
2 Dozers
2 Scrapers
1 Compacter
1 Grader
2 Water Trucks
1 Tractor Mower
4 Pickup Trucks
1 Lowboy Trailer
1 Dump Truck
Miscellaneous
1 Dozer (Spare)
1 Wheel Loader (Spare)
Total Equipment Cost
Equipment Hours per Year
Item
Track Loader, 170FWHP
Track Loader, 275FWHP
Dozer, 125FWHP
Scraper, 18/26 C.Y.
Compacter, 400FWHP
Grader, 125FWHP
Water Truck
Tractor Mower
Trailer
Dump Truck
Dozer, 125FWHP (Spare)
Wheel Loader, 130FWHP (Spare)
Annual Equipment Operator Hours

Labor Hours Per Year
Type Site 1
Equip. Operators 2,452
Laborers
Foremen
Gatekeeper 2,080

Site 1 Site 3 Site 5
$467550 ~^ $757550
$35,000
25,000
74,000
2,500 5,000 12,500
4,000 8,000
200 400 1,000
4,000 4,000 4,000
1,750 1,750 1,750
3,000 3,000 3,000
1,600 2,200 4,000
8,750 8,750 8,750
10,500 10,500 10,500
$78,300 $99,600 $197,500
$475,000

Site 1 Site 3 Site 5
2,080 ~^~ ~~^
2,496
3,744
(1,248)
2,496
248 500 1,248
624 1,248
124 250 624
(25) (25) (25)
(50) (50) (50)
(50) (50) (50)
(50) (50) (50)
2,627 6,541 57557"

2,452 5,118 8,112

Site 3 Site 5 Site 7
sTTTS 87TTJ sTTO
4,160 8,320 4,160
2,496 2,496 2,496
3,744 3,744 3,744

Site 7
—
$35,000
25,000
—
5,000
4,000
400
4,000
1,750
3,000
2,200
8,750
10,500
$99,600


Site 7
' — 	
—
3,744
(1,248)
—
500
624
250
(25)
(50)
(50)
6^

5,118

Total
537550
16,640
7,488
13,312
                              Exhibit 111-7, Page3

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                                  EXHIBIT III - 8
                 COST ESTIMATE - SOLID WASTE DISPOSAL FACILITY
                   E. POTTAWATTAMIE CO. LANDFILL SITE NO. 8

BASIC COST DATA

I.     Land Cost

       E. Pottawattamie Co. Site (8) 40 Ac. g> $500/Ac.                       $20,000

2.     Initial Site Development











3.
4.



5.






6.


7.


8.
Equip. Bldg. &
Pers. Facilities
VVoreroiain 1000'
Perim. Fence 4500'
Entr. Fence 800'
Gravel, Surfacing
Grading
Landscaping
Yard Lighting
Apron Pavement
Miscellaneous

$10,000
5,000
2,300
1,600
900
3,000
2,000
1,000
2,000
1,200











Annual Site Maintenance & Development
Equipment Purchase
1 Track Loader
1 Pickup Truck
Miscellaneous
Equipment Maintenance,
Item
Loader, 115FWHP
Grader, 125FWHP
Mower
Pickup Truck
Miscellaneous
Labor
Full Time
Part Time
Agency Hdqtrs. & Moint.
(130, 000 x .08718 = 11
28,200 x )1)35() =
Agency Operations

$28,000
4,000
1,000
Operation and Amortization
HrsAr. Rate/Hr.
1,560 $7.00
200 5.50
100 2.00



2,080Hr. @4.25 =
300 Hr. @4.25 =
Bldg.
,350)
400






Cost/Yr.
$10,900
1,100
200
1,000
200

$8,800
1,300




                                                                         $29,000

                                                                         $ 1,500
                                                                         $33,000
                                                                         $13,400
                                                                         $10,100
                                                                         $   400
               (65,000)  =                                                $ 2,600

9.     Miscellaneous & Contingency                                          $ 2,000
                               Exhibit 111-8, Page 1

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 ANNUAL COSTS

 I.     One-Time Expense
          (crf-6%-20 Yr.) =  .08718
       Land Cost
       Initial Site Development
       Equip.  Purchase
2.     Reoccurring Annual Expense

       Site Maintenance & Development
       Equip. M.O. 4 A.
       Labor
       Hdqtrs. Bldg.
       Agency Operation
       Miscellaneous & Contingency
       Total Annual Costs
 FIXED & VARIABLE ANNUAL COSTS
                                        .08718
                                       Fixed Costs
       One-Time Expense                $7,200
       Annual Development
       Equip. M.O. & A.                 2,500
       Labor                            1,300
       Hdqrs. Bldg.                        400
       Agency Operation                 2,600
       Miscellaneous & Contingency
QUANTITIES  FOR UNIT AND TOTAL COSTS
       IsfYr., 1970
       4th Yr., 1973
UNIT AND TOTAL COSTS
                       Ac.-Ft.
                       STJ—
                       21.0
                                        $20,000
                                        29,000
                                        33,000
                                        ~
                                        Variable Costs

                                        $  1,500
                                          10,900
                                           8,800
                                                          2,000
                                                        $23,200
Tons
2oV200
25,000
                                                                         $ 7,200
                                                                         $30,000

                                                                         $37,200
       1st Yr., 1970    23.5 Ac. Ft.     28,200 Tons
       Fixed Cost      $14,000 - 23.5 Ac.  Ft. =
       Variable Cost    23,200 r 23.5 Ac. Ft.  =
                      $37,200
       $38,200 .. 28,200 Ton  =          $! .36/Ton

                       21 Ac. Ft.       25,000 Tons
       4th Yr., 1973
       Fixed Cost
       Variable Cost 21  Ac, Ft. x $990/Ac. Ft.
       $34,800*21 Ac. Ft.  =
        34,000s- 25,000 Ton =

BOND DEBT SERVICE RESERVE
                                       $595/Ac.  Ft.
                                        990/Ac.  Ft.
                                     $l,58"37Ac.  Ft.
                                       $14,000
                                        20,800
                                       $34,800
                       $l,660/Ac. Ft.
                       $l.39/T°n
       0.4(7200) = $1800
       IstYr.    1,800 <• 28,200 Ton =    $0.07/Ton
       4th Yr.    1,800 <. 25,000 Ton =    $0.08/Ton
SUMMARY OF UNIT COSTS
       Year
       T970
       1973
Operation Cost
$/Ton	
$1 .36
 1.39
                                       Debt Service
                                       Reserve Cost
                                       $A°"
                                        0.08
                               Exhibit 111-8, Page 2

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 EXHIBIT IV -1  METHODS OF DETERMINING A FEE FOR REFUSE DISPOSAL

 There are four methods, in common usage, that are used to determine the fees
 collected for the use of disposal sites.  Each method is basically an approach to
 measuring the quantity of waste as delivered to the landfill site,  so that a fee
 schedule may be adopted which will produce sufficient revenue to support the dis-
 posal operation.   The four  methods include:

        1.    Fees based on tonnage of actual waste;
        2.    Fees based on the gross vehicle weight;
        3.    Fees based on the gross volume of the hauling vehicle;
        4.    Fees based on the volume of actual waste.

 All of these methods have advantages and disadvantages.  The tonnage basis is
 recommended as being the  fairest, most accurate and most practical to operate.

 This  method has the greatest initial cost because a scale house and scales must
 be installed.  This cost has been estimated and is included in the landfill site
 development costs presented in Part Three.

 Each vehicle is weighed upon entering the site and the gross weight of the vehicle
 and load is automatically recorded on the scale mechanism and on a weight ticket.
 Upon exiting the site, the empty or tare weight of the vehicle  is recorded, on the
 weigh ticket, the net weight of the  refuse and the fee is  determined and recorded
 on the ticket automatically.  The driver then pays the fee with a credit card, or uses
 prepaid coupons or may pay in cash.

 This  method is accurate and convenient,  and removes any individual judgment
 determination by employees or drivers.  In addition, an efficient method of  record
 keeping and billing is built  into the system.  The fee based on tonnage of actual waste
 is also  reasonably fair.   Where there is a inequity in the fee based on tonnage,
 either for the waste producer or the disposal facility operator, a special fee may
 be determined for the class of material involved.  The rate setting authority should
 be empowered to adjust rates as required.

 Determining the fee by gross  vehicle weight or by gross volume of vehicle are
 both similar in procedure and method.  They have the advantage of not requiring
 any initial investment.  The inequities in these methods are great.  As often as
 not, the weight or capacity  of  the vehicle has no bearing on the actual amount of
refuse hauled in the vehicle.  Customers carrying small or partial loads are
 penalized while those who overload their vehicles  receive a premium.  In order
 to keep customer dissatisfaction to a minimum,  a great deal of individual spot
 adjustments and determinations must be made by the landfill attendant.  This leads
 to a general breakdown of cost and scheduling  procedures.   These methods are
 considered satisfactory on  an interim or short time basis, where it would not be
 practical or economical to install scales.
                                Exhibit IV-1,  Page 1

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The method of determining fees by actual volume of the waste is
essentially a fair method, similar to the tonnage system,  but it
too has possibilities of inequities.  The volume occupied by a
given quantity  of waste will vary with the type of material and how
it is precompacted or loaded.  This method has the advantage of
not requiring scales and would be suitable at a location too small
to afford the expense of scales or for a temporary fee system.
                             Exhibit IV-1,  Page 2
                                          iS V. S. GOVERNMENT PRINTING OFFICE : O - 424-632

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