Summaries of Solid Waste Research
     and Iraiaing Grants-1970

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                             ADDENDUM*

                                    TO

  "SUMMARIES  OF SOLID WASTE  RESEARCH AND  TRAINING  GRANTS-1970"  -  SW-5r.2

                          RESEARCH GRANTS ONLY
                         THROUGH JULY 31, 1971
STABILIZING SANITARY LANDFILLS BY INJECTION GROUTING

Dr. Lyle K. Moulton                     EP 00016-02
Department of Civil Engineering         Support to date:  $80,550
West Virginia University                Terminates:  January 1973
Morgantown, West Virginia 26506

DESIGN OF A WATER DISPOSABLE PACKAGING CONTAINER

Dr. Samuel F. Hulbert
Division of Interdisciplinary Studies   EP 00033-04                                   \
Clemson University                      Support to date:  $219,982
Clemson, South Carolina 29631           Terminates:  February 1972

UTILIZATION OF BROILER LITTER AS ANIMAL FEED

Dr. Joseph P. Fontenot                  EP 00034-03
Department of Animal Science            Support to date:  $102,247
Virginia Polytechnic Institute          Terminated:  May 31, 1971
Blacksburg, Virginia 24601

THE TREATABIHTY OF LEACHATE FROM SANITARY LANDFILLS

Dr. Robert K. Ham                       EP 00041-02
Department of Civil Engineering         Support to date:  $32,707
University of Wisconsin                 Terminates:  May 1972
Madison, Wisconsin 53706

POLLUTION OF SUBSURFACE WATER BY SANITARY LANDFILL

Dr. Alex A. Fungaroli                   EP 00162-05
Department of Civil Engineering         Support to date:  $455,648
Drexel University                       Terminates:  August 31, 1972
Philadelphia, Pennsylvania 19104

CHEMICAL TRANSFORMATION OF SOLID WASTES

Dr. Virgil H. Freed                     EP 00242-05
Department of Agricultural Chemistry    Support to date:  $176,695
Oregon State University                 Terminates:  September 30, 1971
Corvallis, Oregon 97331

^Budget and administrative changes that have developed since printing of the
 full text are reflected in this Addendum.  Prefix "EC" automatically changed
 to "EP" on all solid waste research grants active  as  of June  28, 1971.

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EFFECTS OF GARBAGE COMPOST ON SOIL PROCESSES

Dr. Charles C. Hortenstine             EP 00250-05
Department of Soils                    Support to date:   $89,423
University of Florida                  Terminates:  November 30, 1971
Gainesville, Florida 32601

STUDIES OF MODIFICATIONS OF SOLID INDUSTRIAL WASTES

Dr. Cornelius S. Grove                 EP 00257-03
Department of Engineering              Support to date:   $157,518
Syracuse University                    Terminates:  June 1971
Syracuse, New York 13210

COMPREHENSIVE STUDIES OF SOLID WASTE MANAGEMENT

Dr. Clarence G. Golueke                EP 00260-05
University of California               Support to date:   $938,273
Richmond Field Station                 Terminates:  May 31, 1972
Richmond, California 94720

STUDY OF INSTITUTIONAL SOLID WASTES

Professor Jerry C. Burchinal           EP 00265-02
Department of Civil Engineering        Support to date:   $120,037
West Virginia University               Terminated:  June 30, 1971
Morgantown, West Virginia 26506

ANIMAL WASTE COMPOSTING WITH CARBONACEOUS MATERIAL

Dr. William S. Caller                  EP 00270-03&S1
Department of Soil Science             Support to date:   $67,437
North Carolina State University        Terminates:  November 1971
Raleigh, North Carolina 27607

WASTE COMPOSTS AS CHELATING AGENTS IN PLANT NUTRITION

Dr. Willard L. Lindsay                 EP 00273-03&S1
Department of Agronomy                 Support to date:   $59,740
Colorado State University              Terminates:  September 1971
Fort Collins, Colorado 80521

UTILIZATION OF FIBROUS WASTES AS SOURCES OF NUTRIENTS

Dr. James M. Leatherwood               EP 00274-04
Department of Animal Science           Support to date:   $108,526
North Carolina State University        Terminates:  January 1972
Raleigh, North Carolina 27607

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UTILIZATION OF BARK WASTE

Professor Raymond A. Currier            EP 00276-04
Forest Research Laboratory              Support to date:   $212,478
Oregon State University                 Terminated:  May  1971
Corvallis, Oregon 97331

SOLID WASTE DISPOSAL AND BIRD HAZARD TO AIRCRAFT

Dr. Howard L. Cogswell                  EP 00277-03
Department of Biological Science        Support to date:   $63,123
California State College                Terminates:  November 1971
Hayward, California 94542

LASER MEDIATED LIGNIN SOLID WASTE FERMENTATION

Dr. Donald A. Klein                     EP 00278-03
Department of Microbiology              Support to date:   $48,303
Oregon State University                 Terminates:  May  30,  1972
Corvallis, Oregon 97331

DECISION MAKING AND SOLID WASTE DISPOSAL

Dr. John R. Sheaffer                    EP 00281-02
Center for Urban Studies                Support to date:   $201,008
University of Chicago                   Terminated:  April 1971
Chicago, Illinois  60637

A RECIRCULATING WASTE SYSTEM FOR SWINE UNITS

Dr. Ronald J. Miner                     EP 00283-03
Department of Agricultural Engineering  Support to date:   $58,153
Iowa State University                   Terminates:  November 1971
Ames, Iowa 50010

THERMOPHILIC METABOLISM IN SOLID SUBSTRATES

Dr. Marvin E. Stephenson                EP 00292-03
Department of Civil Engineering         Support to date:   $105,625
Michigan State University               Terminated:  May  31,  1971
East Lansing, Michigan 48823

SURVIVAL OF PATHOGENS IN ANIMAL MANURE DISPOSAL

Dr. Stanley L. Diesch                   EP 00302-03
Dept. of Veterinary Microbiology        Support to date:   $116,208
  and Public Health                     Terminates:  May  1972
University of Minnesota
Minneapolis, Minnesota 55455

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INCINERATION OF PLASTICS FOUND IN MUNICIPAL REFUSE
Dr. Richard W. Heimburg
Department of Mechanical Engineering
Syracuse University
Syracuse, New York 13210
EP 00304-03&S1
Support to date:  $313,487
Terminates:  February 1972
ENGINEERING PROPERTIES OF COMPACTED ASH FILLS
Dr. Donald H. Gray
Dept. of Civil Engineering
University of Michigan
Ann Arbor, Michigan 48104
EP 00317-02
Support to date:  $40,455
Terminated:  April 1971
WOOD WASTE REUSE IN CONTROLLED RELEASE PESTICIDES
Dr. G. Graham Allan
Institute of Forest Products
University of Washington
Seattle, Washington 98105
EP 00319-03&02S1
Support to date:  $116,644
Terminates:  May 1972
FIRESIDE METAL WASTAGE IN MUNICIPAL INCINERATORS
Dr. Paul D. Miller
Department of Chemistry and Biology
Battelle Memorial Institute
Columbus, Ohio 43201
EP 00325-03&S1
Support to date:  $342,964
Terminates:  February 1972
CONVERTING INCINERATOR RESIDUE TO USEFUL MATERIALS
Dr. Peter E. D. Morgan
Franklin Institute Research Labs.
20th and Benjamin Franklin Parkway
Philadelphia, Pennsylvania 19103
EP 00326-02
Support to date:  $99,957
Terminated:  April 30, 1971
SINGLE CELL PROTEINS FROM CELLULOSIC WASTES
Dr. Charles R. Dunlap
Department of Chemical Engineering
Louisiana State University
Baton Rouge, Louisiana 70803
EP 00328-03
Support to date:  $286,854
Terminates:  February 1973
USE OF DOMESTIC WASTE GLASS FOR URBAN PAVING
Dr. Ward R. Malisch
Department of Civil Engineering
University of Missouri
Columbia, Missouri 65401
EP 00329-03
Support to date:  $101,405
Terminates:  May 1972

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CRITERIA FOR DESIGN AND CONTROL OF INCINERATORS

Dr. Adel F. Sarofim                     EP 00330-03
Department of Chemical Engineering      Support to date:  $193,192
Massachusetts Inst. of Technology       Terminates:  May 1972
Cambridge, Massachusetts 02139

NATIONAL INDUSTRIAL SOLID WASTE MANAGEMENT CONFERENCE

Dr. H. Nugent Myrick                    EP 00331-01
Department of Environmental             Support to date:  $29,500
  Science and Engineering               Terminated:  April 30, 1971
University of Houston
Houston, Texas 77004

STANDARD TEST PROCEDURES FOR MUNICIPAL SOLID WASTES

Dr. Russell H. Susag                    EC 00332-01
University of Florida                   Support to date:  $38,887
Gainesville, Florida 32601              Terminated:  May 31, 1971

REFUSE RECLAMATION BY SIZE REDUCTION AND SEPARATION

Dr. David G. Wilson                     EP 00333-03
Department of Mechanical Engineering    Support to date:  $218,748
Massachusetts Inst. of Technology       Terminated:  June 1973
Cambridge, Massachusetts 02139

RECLAMATION OF ENERGY FROM ORGANIC REFUSE

Dr. John T. Pfeffer                     EP 00364-02
Department of Civil Engineering         Support to date:  $75,850
University of Illinois                  Terminates:  July 1972
Urbana, Illinois 61801
CHEMICAL CONVERSION OF WOOD AND CELLULOSIC WASTES

Dr. Fred Shafizadeh                     EP 00370-01
Department of Chemistry                 Support to date:  $36,458
University of Montana                   Terminates:  February 1974
Missoula, Montana 59801

COMBUSTION PRODUCTS FROM THE INCINERATION OF PLASTICS

Dr. Edward A. Boettner                  EP 00386-02
Department of Industrial Health         Support to date:  $82,711
University of Michigan                  Terminates:  July 1972
Ann Arbor, Michigan 48104

MARINE DISPOSAL OF FINE-GRAINED WASTE SOLIDS

Dr. M. Grant Gross                      EP 00388-02
Marine Sciences Research Center         Support to date:  $176,151
State University of New York            Terminates:  January 1972
Stony Brook, New York 11790

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RESEARCH ON AN ANIMAL WASTE POLLUTION CONTROL SYSTEM
Dr. Elihu D. Grossman
Dept. of Chemical Engineering
Drexel Institute of Technology
Philadelphia, Pennsylvania 19104
EP 00390-02
Support to date:   $91,373
Terminates:  July 1972
PREVENTING LANDFILL LEACHATE CONTAMINATION OF WATERS
Mr. Eddie J. Wren
Dept. of Environmental Science
Plantation Park Laboratories
Baton Route, Louisiana 70808
EP 00393-02
Support to date:  $95,790
Terminates:  January 1972
HIGH ENERGY GAS FROM REFUSE USING FLUIDIZED BEDS
Dr. Richard C. Bailie
Dept. of Chemical Engineering
West Virginia University
Morgantown, West Virginia 26506
EP 00399-03
Support to date:  $293,556
Terminates:  June 1972
REUSE OF PLASTICS RECOVERED FROM SOLID WASTES
Dr. Donald R. Paul
Dept. of Chemical Engineering
The University of Texas
Austin, Texas 78712
EP 00411-01
Support to date:  $23,342
Terminates:  July 1973
SOLID WASTE CELLULOSE DEGRADATION BY THERMOACTINOMYCES
Dr. Fred J. Stutzenberger
Department of Microbiology
Weber State College
Ogden, Utah 84403
EP 00420-01
Support to date:  $9,982
Terminated:  November 1971
STUDY OF ECONOMICS OF HOSPITAL SOLID WASTES SYSTEMS
Dr. Richard G. Bond
School of Public Health
University of Minnesota
Minneapolis, Minnesota 55455
EP 00458-02
Support to date:  $94,956
Terminates:  May 1972
TIME-SETTLEMENT OF BEHAVIOR OF PROCESSED REFUSE
Dr. Arley G. Franklin
Department of Civil Engineering
Northwestern University
Evanston, Illinois 60201
EP 00466-01
Support to date:  $32,886
Terminates:  February 1973

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SCRAP RUBBER TIRE UTILIZATION IN ROAD DRESSINGS

Mr. Benson G. Brand                     EP 00500-01
Polymer and Paper Technology Division   Support to date:   $51,018
Battelle Memorial Institute             Terminates:  May 1974
Columbus, Ohio 43201

NATIONAL CONFERENCE ON SOLID WASTE DISPOSAL SITES

Mr. George M. Tomsho                    EP 00502-01
American Public Works Association       Support to date:   $32,355
Chicago, Illinois 60637                 Terminated:  June 30, 1971

SOLID WASTE CONVERSION:  CELLULOSE LIQUEFACTION

Dr. Alvin H. Weiss                      EP 00516-01
Chemical Engineering Department         Support to date:   $75,901
Worcester Polytechnic Institute         Terminates:  February 1973
Worcester, Massachusetts 01609

FABRICATION OF SINGLE CELL PROTEINS FROM CELLULOSIC WASTES

Dr. William H. Daly                     EP 00524-01
Department of Chemistry                 Support to date:   $14,888
Louisiana State University              Terminates:  July 1973
Baton Rouge, Louisiana 70803

ANALYSIS MODELS FOR SOLID WASTE COLLECTION

Mr. David H. Marks                      EP 00552-01
Department of Civil Engineering         Support to date:   $38,615
Massachusetts Institute of Technology   Terminates:  May 1973
Cambridge, Massachusetts 02139

FORMATION OF SILICON CARBIDE FROM RICE HULLS

Dr. Ivan B. Cutler                      EP 00558-01
Materials Science Division              Support to date:   $21,621
University of Utah                      Terminates:  May 1974
Salt Lake City, Utah 84112

SIZE REDUCTION IN SOLID WASTE PROCESSING

Dr. George J. Trezek                    EP 00570-01
Department of Mechanical Engineering    Support to date:   $20,316
Division of Thermal Systems             Terminates:  May 1973
University of California
Berkeley, California 94720

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BUSINESS ANALYSIS OF THE SALVAGE INDUSTRY
Mr. Robert M. Sontheimer
Resource Planning Institute, Inc.
Suite 7000
1 Broadway
Cambrdige, Massachusetts 02142
EP 00600-01
Support to date:  $60,047
Terminates:  May 1972
ROUTING OF SOLID WASTE COLLECTION VEHICLES
Dr. John C. Liebman
Department of Environmental Health
Johns Hopkins University
Baltimore, Maryland 21218
EP 00602-01
Support to date:  $52,928
Terminates:  May 1973
SANITARY LANDFILL STABILIZATION WITH LEACHATE RECYCLE
Dr. Frederick G. Pohland
Sanitary Engineering Laboratories
School of Civil Engineering
Georgia Institute of Technology
Atlanta, Georgia 30332
EP 00658-01
Support to date:  $24,739
Terminates:  May 1973
THE METALLURGICAL UPGRADING OF AUTOMOTIVE SCRAP STEEL
Dr. Norman 0. Carlson
Ames Laboratory
c/o Iowa State University
Ames, Iowa  50010
EP 00667-01
Support to date:  $39,998
Terminates:  May 1973
AN INFRA-RED SPECTRAL SENSOR FOR REFUSE SORTING
Dr. Frank P. Winkler
Department of Physics
Middlebury College
Middlebury, Vermont 05753
EP 00682-01
Support to date:  $20,735
Terminates:  May 1973
AN EXPERIMENTAL HIGH ASH PAPERMILL SLUDGE LANDFILL
Dr. Orlando B. Andersland
Division of Engineering Research
Michigan State University
East Lansing, Michigan 48823
EP 00685-01
Support to date:  $89,616
Terminates:  May 1973
                                                        ya72-l-14s

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               Summaries of Solid  Waste
        Research and Training Grants-1970
              This publication (SW-5r.2) was compiled by
   Louis W. LEFKE, Sanitary Engineer, ALVIN G. KEENE, Sanitary Engineer.
RICHARD A. CHAPMAN, Sanitary Engineer, and HENRY JOHNSON, Research Chemist
          U.S. ENVIRONMENTAL PROTECTION AGENCY

                   Solid Waste Management Office
                              1971
                Environmental Protection Agency
                Library, ~ : • : r.j /
                1 North y:.,,;;cr Lr-ive
                Chicago, Illinois   60606

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                   ENVIRONMENTAL  PROTECTION  AGENCY

                        An Environmental Protection  Publication
This publication is also in the Public Health Service numbered series, as Public Health Service
Publication No.  1596  (1970).  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. 74-611512
For sale by the Superintendent of Documents, U.S. Government Printing Office, Washington, D.C. 20402 - Price $1.25
                                    Stock Number 5502-0030
              DISCRIMINATION PROHIBITED—Title VI of the  Civil Rights
              Act of 1964 states:  "No person  in  the  United States shall, on the
              ground of race, color, or national origin, be excluded from paitici-
              pation in, be denied the benefits of, or be subject to discrimination
              under  any program or activity receiving  Federal  financial  assist-
              ance."  Therefore,  projects supported  by grants or  awards  from
              the Solid Waste Management Office, like every program or activity
              of the  U.S. Environmental Protection Agency, must be operated in
              compliance with this law.

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                                             FOREWORD

               THIS  PUBLICATION marks  the  third issuance  of  Summaries  oj  Solid Waste
               Research and Training Grants. The purpose of this updated  review  is to
               inform  interested readers of  completed and  active solid waste research
               projects and training programs. It is anticipated and hoped that this  com-
               pilation will assist competent researchers in determining gaps in solid waste
               management knowledge  and  help  to stimulate the  conception  of  new
^_,            approaches  to or  modifications of existing  practices which will  result in
 %"             improved overall solid waste management for the nation.
                   The Bureau of Solid Waste Management, the predecessor of the  Solid
               Waste Management Office (SWMO) was established under authority of the
 '•*             Solid Waste Disposal Act, Public Law 89-272.  Prior to this Act, a modest
 '-             solid  waste research effort (EF series) was supported by  the former Division
               of Environmental Engineering and Food Protection.  The lack of and  need
               for an extensive and concerted research effort  was recognized by  the Congress
 f              in passing the 1965 Solid Waste Disposal Act. The Act authorized initiation
-9             and acceleration of  a national research and  development program for new
l^             and improved methods of proper and economic solid  waste  management.
fO             Grant,  contract,  and  in-house efforts are  coordinated to  meet the Act
^             directives designed to  conserve natural resources, to reduce the amount of
w             wastes and  unsalvageable materials, and  to encourage the recovery and
               utilization of potential resources in solid wastes.
                   There  is probably no single approach applicable to the wide array of
               solid  wastes  generated. Further, solid waste  characteristics  are continually
               changing through product innovations, industrial process modifications, and
               general population  living habit evolution. Solid waste storage,  collection,
               transport, reuse, upgrading, and disposal practices have not kept pace with
               these  changes.
                   The  objective  of the SWMO is  to develop efficient and economical
               solid  waste  management  practices to meet national  needs.  Extramural
               research is supported in practically all phases of the problem,  for example,
               generation,  collection, transport, reuse, health, and  disposal.  Research  ef-
               forts  receive from one to six years support, with the  majority being for
               three years.  Research  results  are beginning  to  accrue  and  this issuance  is
               indicative of this fact. A "Findings" writeup,  which  is included for the
               first time,  describes the major results.  (Mention of commercial products
               does not imply endorsement by the  U.S. Government.) Additional detailed
               information can  be obtained from  the publications listed  for each grant.
               To further  inform the research community,  the SWMO is  planning to
               publish comprehensive final grant reports that contain new  and worthwhile
               information.
                   The  training grant program is an effort  to develop  personnel  with
               advanced technical  know-how and  interest  in  solid waste. Graduate-level
               training is offered to  qualified students in  solid waste-oriented programs.
               It is also the intent of the training program to produce  professional workers

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in the solid waste field who will be qualified to utilize the recommendations
accruing from the research effort.
    The research and training grants described in this publication have
produced worthwhile results that are being implemented, and the ongoing
and planned projects hold the promise  of further aiding the  Nation in
coping with its solid waste problems. The SWMO's grant support program,
integrated with its other efforts, provides a unified vehicle to solid waste
problem solutions.

                                  —RICHARD D. VAUGHAN,
                                     Assistant Surgeon General
                                     Acting Commissioner
                                     Solid  Waste Management Office.

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                                       Contents
                                                                                    PAGE
SECTION  I:  RESEARCH  GRANTS                                                    '
Composts  and  Composting

Composting  Fruit and  Vegetable Refuse (T)	      3
Conservation of Resources in  Municipal Waste  (T)	      4
Nitrogen Cycle Ecology of Solid Waste  Composting  (T)	      5
Animal Waste Composting with Carbonaceous Material (A)	      6
Cellulose Degradation  in  Composting (A)	      8
Effects of Garbage Compost on  Soil Processes (A)	      8
Fate of Insecticides in Composted  Agricultural  Wastes (A)	     11
Waste  Composts as Chelating Agents in Plant Nutrition (A)	     12
Conferences and  Symposiums

Conference of Institute for Solid Wastes  (T)	    13
National Conference on  Packaging Waste Management (T)	    14
National Conference on  Solid Waste  Management (T)	    15
National Conference on Solid Waste Research (T)	    15
National Symposium on  Animal Waste Management  (T)	    16
National Industrial  Solid Waste  Management  Conference  (A)	    16
Containers

Design of a Water-Disposable Packaging Container  (A)	    17




Farm and Field Wastes

A Study of Farm Wastes  (T)	    18
Disposal of Dairy Cattle Wastes  by Aerobic Digestion (T)	    19
Engineering Properties  of Farm Wastes (T)	    21
Handling,  Treatment,  and Disposal of Animal Wastes (T)	    23
Identification of Odors in Feedlot  Operations  (T)	    24
Livestock Waste Management and Sanitation  (T)	    25
Microbiological Stabilization  of  Animal  Wastes (T)	    27
Poultry Manure Disposal  by  Plow Furrow  Cover  (T)	    27
Sanitary  Engineering Applied to Livestock Manures (T)    	    29
A Recirculating Waste  System for Swine Units (A)	    30
Effects of Processing Poultry Manure on Disease  Agents  (A)	    31
Research on Animal Waste Pollution Control  System (A)	    34
Survival of Pathogens in  Animal Manure Disposal  (A)	    35
Hospitals

Bacterial Contamination  from Hospital  Solid Wastes (T)	     36
Incineration of Infectious and Radioactive Solid Waste (T)	     38
Hospital Solid Waste Disposal in  Community Facilities (A)	     39
Study of Institutional Solid Wastes (A)	     40
    (,T?  Terminated 1  as of March 31, 1970
    (A)  Active      f

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Incineration and Incinerators

A  Study of Incinerator Residue (T)	    41
Smokeless Incineration  of  Bulky  Municipal Refuse (T)	    42
Systems Analysis of Shipborne Municipal Incineration (T)	    43
Combustion Products from  the  Incineration of Plastics  (A)	    45
Continuous-feed Incineration of Municipal  Refuse (A)	    46
Criteria for Design and Control of Incinerators (A)	    47
Fireside Metal  Wastage in  Municipal  Incinerators (A)	    48
Incineration of Plastics Found in Municipal Refuse (A)	    49
Insects  and Insecticides
Fly and  Economic  Evaluation  of  Urban  Garbage Systems (T)	    50
Integrated Control  of  the Housefly  (A)	    51
Succession and Ecology of Diptera in Cattle Droppings (A)	    52
Planning and Management

Dynamic  Evaluation  Procedure; Refuse-Handling System (T)	    54
Mathematical Analysis  of  Solid  Waste  Collection (T)	    55
Mathematical Simulation of Refuse Collection and  Disposal Systems (T)	    56
Optimal Policies for  Solid  Wastes  Collection (T)	    57
The Physical and Chemical Composition of Municipal Refuse  (T)	    58
Comprehensive Studies of  Solid Waste  Management  (A)	    60
Decision  Making  and  Solid Waste Disposal (A)	    63
Standard  Test Procedures  for Municipal  Solid  Wastes (A)	    65
Phytotoxins
Biologic Consequences of Plant Residue Decomposition in Soil  (A)	    66
Pyrolysis
Pyrolysis  of  Municipal  Refuse  (T)	    68
Pyrolysis  of  Solid  Municipal Wastes  (A)	    69
Reclamation and Reuse

Citric  Acid from  Citrus  Wastes by Fermentation (T)	    70
Garbage and  Wastes  for  Mushroom Production  (T)	    71
Partial  Oxidation  of  Solid  Organic Wastes  (T)	    72
Useful Disposal of Auto Bodies and Discarded Tires  (T)	    72
Biological  Conversion  on Animal Wastes to  Nutrients (A)	    73
Biological  Methane Formation  (A)	    74
Chemical Transformation of Solid Wastes  (A)	    76
Converting  Incinerator Residue  to  Useful  Materials  (A)	    77
Degradation of  Waste Paper to Protein (A)	    78
Engineering Properties of Compacted  Ash  Fills  (A)	    80
High-Eneigy Gas  from Refuse Using Fluidized Beds  (A)	    81
Kinetics  of Porteous  Refuse Hydrolysis Process  (A)	    82
Laser-Mediated  Lignin Solid Waste Fermentation (A)	    83
Noncombustive  Disposal of  Solid Agricultural Wastes  (A)	    84
Photosynthetic Reclamation  of  Agricultural Solid and Liquid Wastes  (A)	    85
Poultry Offal  Silage as a Feed Ingredient  (A)	    87
Radiolytic  Hydrolysis  of  Cellulose (A)	    87
Reclamation of Energy from Organic  Refuse (A)	    88
Refuse Reclamation by Size Reduction  and Separation (A)	    89

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                                                                                 1'AGE
Single-Cell  Proteins from  Cellulosic Wastes  (A)	    90
Studies on Modifications of Industrial Wastes (A)	    92
Thermophilic Aerobic Process for Waste Treatment (A)	    93
Use of Domestic Waste  Glass for Urban  Paving	    94
Using Wastes Formed in Vegetable and Cheese Production (A)	    95
Utilization  of  Bark Waste (A)	,  ,  ,	    96
Utilization  of Broiler Litter as Animal  Feed (A)	    99
Utilization  of Fibrous Wastes as Sources of Nutrients (A)	    100
Wood  Waste Reuse in Controlled-Release  Pesticides (A)	    102
Safety

Solid  Waste Disposal and Bird Hazard to Aircraft (A)	102



Sanitary Landfill

Microbiology and Acid Production in Sanitary Landfills (T)	105
Sanitary  Landfill  Investigation  (T)	,	106
Special Studies of a Sanitary Landfill (T)	   107
Pollution  of Subsurface Water  by Sanitary Landfill (A)	   109
Preventing Landfill Leachate  Contamination  of Waters (A)	   Ill
Stabilizing  Sanitary Landfills  by Injection Grouting (A)	Ill
Theimophilic  Metabolism in Solid  Substrates	   112
 Sea Disposal
 Marine Disposal of Fine-Grained Waste Solids  (A)	   113
 Transport
 Pipe  Transport of Domestic Solid  Waste (A)	   114
 SECTION II:  RESEARCH GRANT PROJECTS BY STATE AND PRINCIPAL
               INVESTIGATOR                                                    117
 SECTION III: TRAINING GRANTS                                               121
 SECTION IV: RESEARCH AND  TRAINING  GRANT PRINCIPAL
               INVESTIGATORS                                                   131

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    SECTION I



RESEARCH GRANTS

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                        Composting Fruit and Vegetable Refuse
                      Mr. Walter A. Mercer
               National Canners  Association
               Western Research  Laboratory
                Berkeley, California  94710
 Grant No. Ul 00524-04
 Funds Awarded: $102,346
 Project Period: Apr. 1,  1963 to Mar. 31, 1968
OBJECTIVES:  To develop a rapid, aesthetically
acceptable, reliable, and economic method
of  disposing—through  accelerated  aerobic
composting—of  high-moisture  solid  refuse
produced in harvesting and in the processing
of fruits and vegetables.

APPROACH:   Pilot  studies  were  conducted
using aeration  bins  in which mixtures  of
fruit- and vegetable-canning wastes were com-
posted with dry, moisture-absorbing materials
such  as  redwood  bark,  straw, sawdust, rice
hulls, coffee grounds, and final compost from
the process. The effects of repeated additions
of fresh waste with intermittent or continuous
forced aeration  were also investigated.
  Using information obtained by these pilot
bin studies, and parallel to them, large-scale
windrow composting studies were made. The
compost material was  turned and mixed on
a flexible schedule.

FINDINGS:  Ground  fruit waste  required  a
higher  proportion  of  absorbent, but  under
these conditions the time required for  the
completion of a compost cycle was reduced
by 50 percent.  Lags in  the  development  of
desirable  microflora and temperature were
overcome by the addition of  lime, if  caused
by a low pH of the initial compost mixture.
  The addition  of nutrients, such as a nitro-
gen source, stimulated microbial growth and
accelerated  the  compost cycle.  Composted
municipal  refuse  and  rice hulls were two
absorbent materials  that  performed satisfac-
torily without  modification.  Shredded  red-
wood bark failed to  absorb moisture  ade-
quately and  appeared  to  inhibit microbial
growth  because  of its high  tannin  content.
Evaporation during composting of fruit waste
(85 percent moisture)  and microbial  conver-
sion of sugar  and acids to carbon dioxide and
water resulted in substantially reduced weight
and volume of the finished compost. Air-dried
compost could be recycled  as  the absorbent
for fresh waste. The weight and volume  of
the finished compost increased only slightly
when it was recycled several times. Offensive
odors did not develop during the composting
process  nor was fly breeding observed.
  Use  of  the  first  open windrows, having
varied heights and volumes of rice hulls, in-
dicated  that the height of the mass was im-
portant to  efficient composting. Waste could
be  frequently  added  without altering micro-
bial degradation. Thus, open windrows could
not provide the height required for efficient
composting, and it was necessary to  contain
the  compost  mixture  between  permanent
walls.   Forced   aeration—injecting  air  up
through the compost mass—was superior  to
strictly mechanical means of providing aerobic
conditions. Without forced  aeration, anaero-
bic pockets developed  within  the windrow.
Thermophilic  temperatures were  sustained
throughout an operating  season by  applying
waste every day. Wastes were added and the
compost turned at  12-hr intervals;  this  in-
creased  the quantity stabilized within a given
time.  An automated means of turning the
windrow mass was developed. A quarry rock
and gravel  removal machine was modified  to
mix, turn, and aerate the windrows.
  From  a  technologic  standpoint, the com-
post process is a feasible method of stabilizing
high-moisture solid wastes such as those result-
ing from fruit and vegetable processing. Con-
tinuous thermophilic degradation of organic
waste,  sustained  over an  operating season,
provides for the most  efficient stabilization
of wastes with  a given  volume  of absorbent
material. Equipment required  to carry out
an  automated  composted  process has  been
developed and evaluated.  Precise cost figures

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for the operation of full-scale  units are not
yet available.


                PUBLICATIONS

MERCER, W.  A., W. W. ROSE, L. W. RECIER, and J. E.
CHAPMAN.  Better washing of asparagus to improve qual-
ity and prevent spoilage. Research Laboratory Report No.
60—W—46. Berkeley, National Canners Association Research
Laboratories, Western Branch, Feb. 17,  1960.

ROSE,  W. W., J. E. CHAPMAN, and W.  A. MERCER. Com-
posting fruit waste solids. In Proceedings of the Eleventh
Pacific Northwest  Industrial Waste  Conference—1963,
Corvallis, May  9-10, 1963. Oregon State University. (En-
gineering Experiment Station Circular No. 29.)
MERCER, W. A. Industrial solid wastes;  the problems of
the  food industry. In  Proceedings; National Conference
on Solid Waste Research, Chicago, Dec. 1963, University
of Chicago Center for  Continuing  Education. Special
Report No. 29. American Public Works Association, 1964.
p. 51.

ROSE, W.  W.,  and W. A. MERCER. Treatment and dis-
posal of  potato  waste. In Proceedings;  International
Symposium; Utilization  and disposal of potato wastes,
Fredericton, New Brunswick, Canada,  May 24—27,  1965.
New Brunswick Research and Productivity Council, 1966.

ROSE, W.  W., J. E. CHAPMAN, S.  ROSEID, A. KATSUYAMA,
V. PORTER, and W. A.  MERCER.  Composting fruit and
vegetable  refuse.  Compost Science 6(2): 13—25, Summer
1965.
                      Conservation  of Resources  in Municipal  Waste
                   Dr.  Clarence  E. Scarsbrook
         Department of Agronomy  and Soils
                           Auburn  University
                   Auburn,  Alabama   36830
  Grant No. EC  00243-03
  Funds Awarded:  $213,287
  Project Period: Apr.  1, 1967 to Mar.  31,  1970
 OBJECTIVES:   To  evaluate  the use  of com-
 posted refuse  for  agricultural  applications
 ranging from its use as a source of nitrogen
 for  established  grasses  to its  serving as an
 organic additive for production of greenhouse
 container and cut  crops. Compost was also
 evaluated for its use for woody plants, high-
 way planting, and as a cover for revegetating
 areas denuded of  topsoil.  Additional subjects
 were  the  comparison  between   composted
 refuse and peat, sawdust,  and other materials
 as sources  of organic matter in establishing
 grasses, and  also the biological properties of
 compost  when added to soil. Composted gar-
 bage was evaluated  for its effect on the ameli-
 oration of the toxicity of certain  herbicides.

 APPROACH:   Processed municipal solid waste,
 sawdust,  and peat were compared in  experi-
 ments for use on highway median strips, high-
 way  backslopes and  fills,  strip mines, and
 borrow areas.  The effects of these materials
 during the establishment  of different types of
 grasses were determined. The effects of in-
 cluding processed garbage in a hydroseeding
 operation and of  including garbage and acti-
 vated sludge with  peat as a mulching agent
 were  evaluated.  Experiments  compared  am-
 monium nitrate  applied  at  rates  of 80  and
 400 Ib  of nitrogen  per acre  per year  with
 processed garbage.
   Laboratory work involved incubating soil
 samples with compost applied as a mulch and
 as incorporated into  the soil  and determining
 the release  of  CO2,  N, P, and  S. The  C:N
 ratio  as  well as the  development of cation
 exchange capacity  were established.

 FINDINGS:  Garbage  compost  added  at the
 rate  of  100 tons per acre to soils  ranging in
 texture  from loamy sands to clays ameliorated
 the toxicity to  crops  of  certain herbicides
 but  had  no effect on others. Fluometuron
 and trifluralin  (each  at 30 Ib/acre) were  toxic
 to  cotton  without compost additions;  how-
 ever, with compost there was considerably less
 toxicity of the  herbicides on cotton.  Compost
 did not  reduce the  toxicity  of bromacil (50
 Ib/acre), picloram  (30 Ib/acre),  or  simazine
 (30 Ib/acre).
   Garbage  compost,  when  first  applied to
 soils,  was often toxic to seedlings, but  there

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was  little  injury wheti  the -soil was reseeded
4  to 6 weeks  after  application of compost.
The  two  garbage composts  used as received
from the supplier both require large amounts
of N  and P for  plant growth; however,  as
the  compost  ages it  becomes more  nearly
satisfactory  as  a medium  for plant growth.
   The composts compare favorably with hay
and pine straw as a mulch for erosion control.
   The garbage composts used do not appear
promising as a  part of the growth medium for
ornamentals  but  may  be  satisfactory   as
mulches.

                 PUBLICATIONS

ORR, H. P., K. C. SANDERSON,  and \V. C. MARTIN,  JR.
Compaiison  of processed garbage, sawdust, and pine straw
in mulching garden chrysanthemums 1967. Research Re-
sults for  Ninserymen, Auburn Univeisity  Agricultural
Experiment  Station, Horticultural Series No. 10:6, Aug.
1968. (Abstract.)
SANDERSON, K. C.,  H. P.  ORR,  and W. C. MARTIN,  JR.
Compaiison  of processed garbage, sawdust and pine straw
in mulching petunias 1967. Research Results for Nursery-
men, Auburn University Agricultural Experiment Station,
Horticultural Series No.  10:6-7, Aug.  1968. (Abstract.)

SANDERSON, K. C., R. SELF, H. P. ORR, and W. C. MARTIN,
JR. Utilization of processed garbage-sludge as a media ad-
ditive in the production  of woody plants in containers.
Research Results  for Nurserymen, Auburn  University
Agricultural  Experiment Station, Horticultural Series No.
10:5-6, Aug. 1968. (Abstract.)

SANDERSON,  K.  C., H. P,  ORR, and W. C. MARTIN, JR.
Utilization  of  processed  garbage  in  the production of
selected ornamentals. Proceedings; Association of Southern
Agricultural  Workers,  65:160-161, 1968.  (Abstract.)

DICKENS, R., D.  G. STURKIE, J.  D.  MILLER, and J. L.
MORGAN. Utilization of composted  garbage for turf estab-
lishment. Proceedings; Association of  Southern Agricul-
tural Workers,  66:87-88,  1969. (Abstract.)

SCARSBROOK, C.  E. Fertility requiiements of municipal gar-
bage compost foi plant growth. Proceedings; Association
of Southern  Agricultural Workers, 66:96, 1969. (Abstract.)

HILTBOLD, A. E., and  G.  A. BUCHANAN.  Use of  garbage
compost  in  reduction  of  toxic residues  of herbicides in
soil.  Proceedings;  Association of  Southern Agricultural
Workers, 66:102, 1969. (Abstract.)
                   Nitrogen Cycle  Ecology of  Solid Waste  Composting
                           Dr. David  T. Knuth
             Institute of Environmental Studies
                  Gainesville,  Florida   32601
  Grant No. U1-00548-02
  Funds Awarded: $47,540
  Project Period: June 1, 1966 to Sept. 30, 1968
 OBJECTIVES:   To  investigate  the  fate,  re-
 cycling, and  use of nitrogen compounds in
 the composting of solid waste. To investigate
 the kinds  of nitrogen  bacteria present,  and
 to  correlate  nitrogen  products  present with
 microbial  activity.  To predict  and  evaluate
 the effect of environmental changes  on com-
 posting efficiency and on  conditions necessary
 for maximum nitrogen utilization.

 APPROACH:  Composting was   done  in  the
 laboratory to obtain  good  experimental con-
 trol and reproducibility  by using a  specially
 constructed fermenter to simulate the wind-
 row  method  used  in  industrial  operations.
 The  fermenter  was  used  to  obtain  results
 directly applicable to windrow operations  run
 on  the batch  basis,  and, in some  cases, re-
sults were applicable to  continuous thermo-
philic  composting  systems.  The mesophilic,
thermophilic, ambient, and curing stages  of
composting were studied.
   The nitrogen  economy of each  phase was
examined  by  using  wet  chemical,  isotopic,
mass spectrographic, and gas chromatographic
methods.  Microbial nitrogen activity in each
stage  was determined  by  quantitating  the
nitrifying,  denitrifying,  ammonifying,  and
nitrate-reducing  groups. The rate of the com-
posting process was measured in terms of CO2
production  in the  total system, whereas  the
BOD approach was used to measure the de-
gree of stabilization.

FINDINGS:   Some  of  the  soil-nitrogen-cycle
transformations  were  detected  in  the meso-

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philic stage of composting. Inorganic nitrogen
compounds  sometimes accumulated in con-
centrations  representing nearly  20 percent
of the total nitrogen present. Organic nitrog-
enous compounds were hydrolyzed and  am-
monified,  even  though other  organic com-
pounds  in the waste were not noticeably de-
composed. The results suggest  that losses of
nitrogen that may follow ammonification in
subsequent  stages of  composting could  be
prevented by equalizing the rate  of ammoni-
fication  and  the  rate  of  immobilization  by
the composting microflora. No nitrogen  was
lost  either  as  gas  or  as nonexchangeable
nitrogenous  compounds.
  Microbial activity  reached its maximum at
about 12  hours,  declined rapidly  to  about
one-half maximum, and remained at almost
that level for up to 3 or 4 weeks. Microbial
activity did not correlate with the BOD re-
duction  rate, which  declined rapidly after
8 days.
  Nitrogen  transformations play a  critical
role in the  conservation and utilization  of
nitrogen in the composting process. It  is be-
coming increasingly evident that ammonifica-
tion and nitrification must be controlled  or
regulated to  ensure  efficient  utilization  of
nutrient nitrogen. This may be a critical re-
quirement in  substantially improving com-
posting rates  and quality.  Methods used  to
control nitrogen conversions in the soil might
also be applicable in  composting.
               Animal Waste  Composting with Carbonaceous Material
                      Dr. William S.  Caller
                 Department of Soil  Science
             North  Carolina State University
            Raleigh, North Carolina   27607
  Grant No. EC 00270-02
  Funds Awarded: $54,084
  Project Period: June 1,  1968 to May 31, 1971
OBJECTIVES:  To develop a process for com-
posting a combination of chicken manure as
a source of nitrogen and sawdust initially as
a source of carbon to produce a valuable soil
amendment.

APPROACH:   Poultry manure and sawdust are
used as model organic waste materials repre-
senting both  high and low nitrogen-contain-
ing wastes. The carbon-to-nitrogen ratios of
these  materials  are determined. Then the
materials  are mixed to  produce  an  initial
carbon-to-nitrogen ratio of 25:1. The  aerobic
composting characteristics of  this composite
sample  are studied  under controlled  condi-
tions  of temperature to  determine  the opti-
mum temperature for rapid composting. The
C:N  ratio  is then varied to  determine the
optimum mixture  of manure to sawdust. The
moisture  content  of  the mixture  is then
varied to  determine an  optimum condition.
The experiments are conducted in a 45-cu-ft,
horizontal, rotating drum with provisions for
controlling airflow, adding raw material, and
removing finished compost.
   The  microflora found to  be  adapted  to
these conditions are identified and studied
in terms of their physiologic and nutritional
requirements for ensuring maximum compost-
ing rates while an end product that is most de-
sirable as a soil amendment is being produced.
   The final stages of this project involve de-
termining  bulk handling characteristics and
field performance of several possible end prod-
ucts. The compost is being applied at several
rates  to various soils,  and  the response  of
high value crops is  being determined.

FINDINGS:  Batch  composting. The mixture
of sawdust and  poultry manure, blended  in
carbon-to-nitrogen ratios (C:N)  of  25:1  to
40:1, was analyzed chemically and  found  to
be  nutritionally  balanced   for   microbial
growth.  Mixtures of  sawdust and  manure

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ranging from C:N of1 25:1 to 40:1 were then
composted batchwise in the drum composter
with varying moisture contents.
  Maximum  microbial activity was observed
at moisture levels of 55  to 60 percent.  At
more than  65 percent moisture, the mixture
formed  balls that hindered  the  aerobic  ac-
tivity. The moisture content did not vary by
more than  1.2 percent during a given run.
  The oxygen uptake rate for  the C:N mix-
ture of  25:1  was almost 33 percent  greater
than that of  the 40:1 mixture  (4.19 mg of
oxygen per g of volatile solids  versus 3.3 mg
of oxygen per g of volatile solids). Tempera-
tures above 60 C were also sustained almost
three times  longer  for the  C:N  mixture of
25:1. Although  at least 80  percent or more
of the carbon was supplied by the sawdust,
less than 25 percent of the reduction in vola-
tile solids could  be attributed to the sawdust.
Thus, the available carbon  during the  com-
posting  period was  supplied by the manure.
  The  nitrogen loss  during  the  high-rate
composting period averaged only 3.29 percent,
much less than anticipated.
  The maximum time used in studying an
individual  batch was about 5 to 7 days in
the  composter.  Sixteen  batch studies  were
performed.
  After being removed from the composter,
the holocellulose decreased  in content  from
66  to 54 percent and became fairly stable
after 4 weeks. The cation exchange capacity
increased during this period to 69 meq/100 g.
  The  final  compost has  a blackish-white
color and an odor similar  to that  of  fresh
humus soil. Moreover,  the cation  exchange
capacity  is at a level characteristic of a de-
sirable soil conditioner.
  Continuous composter  operation.  During
the period of continuous operation,  poultry
manure was not available and swine manure
was  substituted. A  batch  study showed that
swine manure was satisfactory, although the
mixture  required a week to become thermo-
philic as opposed to 1 to 2 days for the poultry
manure.
  A second batch was started. After the com-
posting mixture had  been  in  the  thermo-
philic  region for 24 hours, one-third of the
mixture was replaced by a fresh manure and
sawdust mixture.  The feeding process was
continued for 2 weeks, after which the process
was allowed to halt. After each feeding, the
temperature dropped from above 60 C  to 45
to 50 C. The 60 C plus temperatures were
again reached after about 6 to 8 hours. The
product removed from the composter appears
similar  to  the  poultry manure-sawdust end
product. Chemical analyses have not yet been
completed.
  Plant growth  studies.  Initial  studies were
made by spreading the compost as a mulch
on patches of grass at the composter site. The
area was  divided into 1.35-sq-m  units and
treated with 0,  3, 6, or 12 qt of compost. No
difference was found among the areas treated
with  compost;   however, the  grass  clipped
from  the  treated areas had a dry-weight  in-
crease  of 22 percent and a nitrogen content
30 percent greater  than  the  untreated areas.
  Greenhouse  studies  using  the  compost
mixed with otherwise untreated soil are being
conducted with  tomatoes, millet, wheat, and
green beans. Ten applications of compost are
being  used  ranging from  0 to 100  percent
compost. When  compared with the 0  percent
treatment, the 10 percent treatment was found
better  for the  tomatoes, millet,  and wheat.
The beans showed  the best growth at the 1
percent level. The increase in dry weight was
found  to  be 400 percent  for  the tomatoes,
354 percent for the millet, 238  percent for
the wheat,  and  153  percent for  the green
beans. The  tomato yield was also greater at
the  10  percent  level.  The bean  seed  yield
was greatest at the  1 percent level as was the
nodule count on the bean roots.
  Tissue studies are in progress. These studies
indicate that the compost  is a valuable soil
conditioner.

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                         Cellulose Degradation in Composting
                          Dr. John S.  Jeris
            Department  of Civil Engineering
                        Manhattan College
                  Bronx, New York  10471
 Grant No. EC 00161-04
 Funds Awarded: $125,872
 Project Period: Aug. 1, 1966 to July 31, 1970
OBJECTIVES:  To  investigate  and determine
the environmental conditions  required for
accelerated cellulose  and refuse degradation
by microorganisms by use of composting pro-
cedures.  To  translate the results into  engi-
neering information so that urban refuse may
be treated more  economically by use of the
compost process.
APPROACH:   Laboratory studies  used a bat-
tery of three  continuously  fed composters.
These bench-scale  studies were  designed  to
determine  the  maximum rate of solid waste
stabilization  under appropriate physical and
chemical   environmental  conditions.  The
study materials included (1) municipal refuse;
 (2)  a  synthetic refuse  composed  of paper,
vegetables, and meat  scraps;  and  (3) paper
with  nutrient  additives.  Cellulose and deg-
radation products  were  assayed so  that  a
measure of  the system's efficiency and  the
metabolic mechanisms could be obtained.
  In conjunction  with the bench-scale com-
posters, Warburg and  shake flask apparatuses
were used  to scan stabilization  rates of  the
solid waste materials over wide ranges of vari-
ous environmental parameters.

FINDINGS:  The maximum rate of municipal
refuse  composting obtained, as measured by
oxygen consumption,  was approximately 50
percent greater than the highest rate reported
in the  literature. At this high rate the signifi-
cant parameters  included (1) a pH of 8 to
8.5,  (2)  a  temperature of 58 to 62 C,  (3) a
nitrogen-to-carbon ratio of 1 to 30,  and  (4)
a moisture content of 65 to 75 percent with
a minimum free-air space of 30 percent.
  The  rate  of  degradation obtained  with
mixed  refuse containing  60  to  70  percent
paper  is about 10 times greater than with a
pure paper solid waste. In  general, an  in-
crease  of paper  content means a  decrease in
stabilization rate owing to the nonbiodegrade-
able nature of paper.
  The stabilization rate decreases significantly
during composting  at  a  material  turnover
rate  greater  than  4 days.  Higher  rates of
biological stabilization are maintained by re-
cycling composted material  as a seed with
fresh refuse. A recycle rate of 50  percent has
given maximum results.
                    Effects  of Garbage Compost on Soil  Processes
                  Dr. Charles C. Hortenstine
                        Department of Soils
                       University of Florida
                  Gainesvile, Florida   32601
 Grant No.  EC 00250-04
 Funds Awarded: $74,161
 Project Period: Dec. 1,  1966 to Nov. 30, 1971
OBJECTIVES:   To evaluate the effects on struc-
ture,  fertility, and  biological activity of add-
ing municipal refuse compost to the soil. To
evaluate the use of compost as a plant nutrient
and to determine  toxic or  beneficial  effects
of compost on  soil when it is applied over
8

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short and long time periods. To evaluate the
water pollution potential of compost.


APPROACH:   Laboratory,   greenhouse,   and
field studies are being conducted concurrently.
Laboratory studies  have been undertaken to
isolate organisms  effective in decomposing
organic refuse. The conditions of tempera-
ture and moisture content of  the  compost
that produce maximum composting rates are
being  determined.  The  compost is being
analyzed for plant nutrients such as nitrogen,
phosphorus, potassium, calcium,  magnesium,
and copper as well as organic matter content.
Laboratory studies are also determining the
water-holding  capacity,  density,  cation  ex-
change  capacity,  and  pH  of  the compost.
Leaching studies  are  being  conducted  to
determine the ground water contamination
potential  of compost.
  Greenhouse studies  are being done to de-
termine  the nutrient availability of compost
as compared with sewage sludge, mineral fer-
tilizers, and animal manures. The potential
of  compost as a  potting medium for  orna-
mental plants is  being thoroughly  investi-
gated.  Soil  characteristics  of  compost  and
compost-soil mixtures are being evaluated to
determine characteristics such as water-hold-
ing  capacity,  pH,  aeration, and drainage
properties.
  Field studies are  being conducted through-
out Florida on major  soil  types  to compare
compost  with other fertilizers as a plant nutri-
ent. Field studies  are  also determining the
maximum amount of  compost that  can  be
mixed with various soil  types without  pro-
ducing conditions toxic to various plants.

FINDINGS:  Composting   municipal   waste
under  controlled  conditions is advantageous
from the following viewpoints: (1) Salvaging
of paper and  metals is  feasible.  (2) There is
no  air or water pollution hazard. (3) There
is no health hazard  due to fly or rodent popu-
lations.  (4) The composted material  may  be
used as a soil-improving amendment.  Munic-
ipal refuse starts, however, as a  waste prod-
uct and remains a waste product throughout
the composting operation.  In other words,
the philosophy that a salable material is pro-
duced from composting municipal  refuse is
not a  valid premise.
  Laboratory. Composted refuse  is variable
in physical makeup and chemical constituents.
This  variability  is  present  between  day-to-
day and season-to-season collections. A typical
sample of composted refuse from the Gaines-
ville plant contained 0.57 percent nitrogen,
0.26 percent phosphorus,  0.22 percent potas-
sium, 33 ppm  boron, 24 ppm manganese, 606
ppm zinc,  1.88 percent  calcium and  0.12 per-
cent magnesium. This  sample  was about 45
percent water  on a wet-weight  basis (79 per-
cent on  dry-weight basis),  38  percent  ash,
2.50 percent total  soluble  salts, and  had a
pH of 6.85.
  In a laboratory experiment where compost
was mixed with Arredondo  fine sand, there
was a  large increase in fungal populations.
Bacterial  populations  also increased after 4
days in soil containing 10  percent  compost,
but these populations decreased again  after a
few days. In carbon dioxide evolution,  com-
post was intermediate  between chicken ma-
nure (which was high) and cow manure (which
was low).  Almost no  nitrification  occurred
where  compost was  added to the soil.  This
was probably due to rapid immobilization of
nitrogen  by the  soil microflora. In applying
compost  to the  soil, this  characteristic must
be compensated  for  either by applying addi-
tional nitrogen or by delaying planting until
the soil microorganisms release nitrogen.  This
delay may be for a period of 3 to 4 weeks or as
long as 6 months, depending on the amounts
of compost applied  and climatic conditions.
  Of  particular  interest  was  the effect of
compost  on nematode survival and  motility.
Where sting nematodes, Belonolaimus longi-
candatus, were  placed in  compost  extract,
motility ceased after  2.8 hours' exposure. This
was attributed to the organic fraction, since
nematodes placed in extract from which the
organic fraction was removed were unaffected.
  In another experiment, survival of African
Giant  earthworms  in  Arredondo fine  sand
was increased by  additions  of  compost. As
little  as  2.5 percent compost  was effective;
however, compost was not as good a medium
for  earthworms as peat.
  Greenhouse. In  several  experiments where
compost  was added to soil, plant growth was

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enhanced. Generally, however, there was an
initial  tieup of nitrogen by soil microorgan-
isms that was detrimental to the  first crop
grown.  Subsequent  crop?  showed  increased
yields as compared with controls only where
large amounts (128 metric tons  or  more per
hectare) of compost were applied. In this re-
spect, compost could not compete with min-
eral fertilizer unless  the compost was free.
  Where compost was applied to soil at rates
of 128 or more tons/hectare, soil phosphorus,
potassium, calcium, magnesium, pH, and total
soluble salts were increased greatly.  Soil phos-
phorus was also  increased at  much lower
rates of compost  (2 tons/hectare). Cation ex-
change capacity and water-holding capacity of
the soil were increased greatly where 128  or
more  tons  of  compost were  applied.  Soil
aeration and granulation were also improved.
In one experiment where 2,048 tons of com-
post were applied per hectare,  aeration was
improved to such an  extent that manganese
was rendered unavailable for plant use. (Plant
roots absorb manganese as the Mn+2 state,
and  oxidation changes it to the Mn+4 state.)
Moreover,  at  such  high rates  total soluble
salts became a  problem, as was manifested
by phytotoxicity in  one crop of radishes.
  Germination.  The effect of compost on seed
germination is of major concern.  In one ex-
periment, compost was extracted in 500 ml
of water, and  the extract was  used  as a mois-
tening  agent  for seed germination.  Where
80 g of compost were extracted, radish seed
germination was reduced to 56 percent.  Ex-
tract from 160 g of compost  reduced radish
seed germination to  16 percent and turnip
seed germination to 40 percent.  Extract from
320  g  of compost reduced  germination of  all
seeds tested—radish to zero, turnip to zero, oat
to 41 percent, and pearl millet to 45 percent.
Seedlings that made any growth in the 320-g
extract showed evidence of phytotoxicity and
were much smaller than seedlings in the other
extracts. The phytotoxic effects  were thought
to be  the  result  of total  soluble salts since
conductivity was increased  greatly  as  the
amounts  of compost extracted increased—
from 1.97 millimhos per cm in  10  g to 26.60
millimhos per cm in 320 g (more than 8 mil-
limhos per cm is considered a strongly saline
solution). This  soluble salt effect is another
indication that there should be a time lapse
between  applications of compost to seeding,
so that leaching of soluble salts below  the
root zone can be allowed for.
  Field experiments. A study was conducted
on  Leon fine sand  to determine the effects
of compost  applications on nematode popu-
lations. Where 8, 16, and 32 tons of compost
per hectare were applied, spiral nematodes,
Helicotylenchus spp., were  reduced in num-
ber as compared with lower  compost rates
or  mineral  fertilizer.  Ring  nematodes, Cir-
conemoides spp., were  also lower  in plots
where 32 tons of compost  per hectare were
applied.  Dorylaims  and   Rhafditids  were
significantly higher  in  soil  from the 32-ton-
per-hectare plots.
  An  experiment  initiated 2  years ago at
International  Minerals Corporation,  Bartow,
Florida, shows promise of yielding invaluable
information. This  experiment  was  designed
to  determine  the effects of adding compost
to  the sand fraction left as a  waste  product
after  the flotation  process, which removes
phosphorus from the matrix. Two rates  (35
and 70  tons  of compost/hectare) were  ap-
plied to plots on this  sand during April of
1968  and 1969. Mineral fertilizer (10-10-10)
was also applied to  plots with no compost  and
to plots where the compost  was applied. Two
crops  (sorghum  and oats)  were grown each
year.
   Oats were not harvested  in  1969. Oats are
growing, however, in the plots  receiving com-
post  only  where  there were  no surviving
plants in  1968.  There was  undoubtedly  a
residual  effect from compost applied in 1968.
This was also shown by much larger sorghum
seedhead yields (272 g overall average in 1968
as compared with 669 g in  1969). In addition
to yield benefits, there was a small but highly
significant increase in  cation  exchange ca-
pacity and water-holding capacity of the sand
as the result of compost application.
   Summary. Research to date has shown  that
composted municipal refuse applied to soil  is
beneficial both to plants and the soil. In order,
however, to reap any benefit  from compost,
relatively large amounts must  be applied  to
the soil.  In  other  words,  the soil must be
considered  as a solid  waste  disposal  sink.
Any  detrimental effects to the soil or plant
 10

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life will soon dissipate «under .favorable clima-
tic conditions.
  Laboratory  research  indicated that  com-
post applied to the soil reduced nitrification
to almost zero. This may  have great implica-
tions in the field in conjunction with animal
waste management. Of major concern  where
animal wastes are applied to the soil is move-
met  of  nitrates into  potable  water  supplies.
An experiment was recently initiated in which
various  levels of compost were  applied to
soil  in small  lysimeters.  The  objective is to
study the  effects  on  nitrification when  cow
manure is applied to the same soil. If com-
post does reduce  or delay the  movement of
NOa  into  ground water  supplies,  this  will
certainly be a worthwhile finding.
                PUBLICATIONS

ROTHWELL,  D. F.,  and C. C. HORTENSTINE. Composted
municipal refuse:  Its  effects on carbon dioxide, nitrate,
fungi, and  bacteria in Arredondo fine sand.  Agronomy
Journal, 61 (6): 837-840, Nov.-Dec. 1969.

HORTENSTINE, C. C., and D. F. ROTHWEJL. Gaibage com-
post as a source of plant nutrients for oats and radishes.
Compost Science, 9(2):23-25, Summer, 1968.

HORTENSTINE, C   C.,  and  D. F. ROTHWELL.  Utilizing
municipal refuse in reclaiming phosphate mining spoil
areas. Presented at Annual Meeting, Association of South-
ern Agricultural Workers, Memphis, Feb. 2—4, 1970.

ROTHWELL, D. F., and C. C. HORTENSTINE. Effect  of com-
posted municipal  refuse and  other organic  wastes on
microbial activity. Presented  at Annual Meeting,  Asso-
ciation of Southern Agricultural Workers, Memphis, Feb.
2-4, 1970.
                 Fate  of Insecticides in Composted Agricultural  Waste
                        Mr. Walter W. Rose
                Western Research Laboratory
                National Canners Association
                 Berkeley,  California   94710
 Grant  No.  EC 00264-04
 Funds  Awarded:  $74,356
 Project Period:  May  1, 1966 to Aug, 31, 1970
OBJECTIVES:   To determine the  fate  of  in-
secticides in  composting  agricultural  wastes
by isolation, separation, and identification of
residues of the  original  insecticide and  its
major transformation  products.  Representa-
tive  insecticides  of the three  major classes,
i.e.,   chlorinated  hydrocarbon,  organophos-
phate,  and   carbamate,   were  incorporated
singly and  as mixtures  in tomato,  peach,
potato, and fresh produce market wastes be-
fore  composting. The effect of both  continu-
ous and batch-type composting operations on
the breakdown of insecticides  was evaluated
by using pure cultures of microorganisms pre-
dominating in the  aerobic compost process.

APPROACH:   Wooden bins  capable  of  hold-
ing 1  cu yd of compost material were filled
with  the proper ratio of organic  waste and
absorbent material. The  waste material was
analyzed  for  field-applied  insecticides,  and
then  purified insecticides  were added  in the
following concentrations:  7 to 20 ppm DDT,
1 to 5 ppm dieldrin, 2 to 10 ppm parathion,
1 to 5 ppm Diazinon®, 10 to 25 ppm Sevin®,
and 5 to  15  ppm zineb.  Regularly scheduled
samples were  taken during the composting
and curing periods and,  after extraction and
purification, were  analyzed  by gas, paper, or
thin-layer chromatography with the addition of
infrared spectroscopy on unknown products.
  In the  composting system whereby specific
insecticides are  markedly  degraded,  the re-
sponsible organism was isolated and cultured.
These pure culture studies  provided samples
from which  degradation products of the in-
secticides could be readily isolated and iden-
tified. The pure  culture studies also estab-
lished the ability of selected microorganisms
to attack  the test insecticides  under  the pre-
vailing pH,  temperature, and moisture  con-
ditions of the compost mixture.

FINDINGS:  The  batch-type and  continuous
thermophilic  compost  procedures  effectively
reduced the levels of  organophosphate- and
                                                                                          11

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carbamate-type insecticides. Degradation was
faster in  the thermophilic process.  For ex-
ample, to reduce the Diazinon concentration
by 50 percent it took 10 days  at thermophilic
temperatures  and 28 days in the  batch-type
system.
  Known degradation products for Diazinon
included oxodiazinon and sulphotepp. Break-
down products for parathion  included amino
parathion,   p-aminophenol,   and   p-nitro
phenol.
  Results for  the  chlorinated  hydrocarbons
support the  finding by others  in regard to
their long persistence.  There was a gradual
loss  of  pp DDT during composting at 110
to 140  F. At lower temperatures there was
no loss, and  this indicated that the observed
decline in DDT was probably due to volatili-
zation. Dieldrin was less persistent  than DDT
and  the batch-type  process was more effective
than the thermophilic process. After 75 days
of composting, the dieldrin concentration ap-
proached  a nondetectable level  in the batch-
type process. For the same  time interval the
thermophilic  process showed  a reduction of
50 percent.  Known breakdown products for
DDT and dieldrin were not  detected in the
compost samples.
  The  two  carbamates, carbaryl  and zineb,
disappeared very rapidly from both  compost
systems.  The  persistence  of  carbaryl  was
found to be  highly dependent upon the pH.
Alkaline pH's accelerated its hydrolysis. Lab-
oratory  studies with  buffered insecticide  so-
lutions  confirmed the  effect  of pH on car-
baryl.  At a  pH of  8.0 or  9.0  the initial
concentration of 60 ppm was  reduced to a
nondetectable level within 22  days.  At pH
7.0 approximately 80 percent of trie carbaryl
was lost within 50 days. At pH  4.0 very little
change  had  occurred  in  the  concentration
after 50 days of incubation.
  Bacteria were the most predominant type of
microorganisms  with both methods.  Actino-
mycetes were next, followed by  fungi. The
type of insecticide used apparently had  no
influence  on  the microflora  that developed
within the compost mass.
  The total numbers of bacteria were about
equal with  both processes. The  numbers  of
actinomycetes and fungi  were  higher with
the batch-type procedure.  There  was a slight
decline  in the total numbers of  each micro-
flora with time of composting.
  Incubation of compost extract in  a mineral
salts medium and  in  insecticide resulted  in
the isolation of some microorganisms. By this
procedure six isolates  have  been  obtained
that grow in the  presence of  Diazinon  or
parathion. One  isolate has  been  obtained
from  the  dieldrin  extracts. Further  work
should provide  additional isolates  for study
in determining a pattern  of insecticide utili-
zation and degradation.


               PUBLICATIONS

ROSE, W. W., W. A. MERCER, A. M. KATSUYAMA, S. ROSEID,
V. Y. PORTER, J. T. YAM ADA, J. A. HESP, and J. MARANO.
Fate of insecticides in composted  agricultural wastes.  Un-
published data. [1967.]
FARROW, R.  P., E. R. ELKINS,  W. W. ROSE, F. C. LAMB,
J. W. RALLS, and W.  A. MERCFR.  Canning operations  that
reduce  insecticide levels in  prepared foods and in solic!
food wastes. Residue  Reviews, 29:73-87, 1969.
               Waste  Composts  as Cheiating Agents in  Plant Nutrition
                      Dr. Willard L. Lindsay
                  Department of Agronomy
                  Colorado State University
               Fort Collins,  Colorado   80521
 Grant No.  EC 00273-02
 Funds Awarded: $36,945
 Project Period: June  1, 1968 to May 31, 1971
OBJECTIVES:   To test the hypothesis that com-
posts and related organic  materials  either
contain or  can produce  organic compounds
capable of  chelating insoluble nutrient ele-
12

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ments in the soil. The addition of such com-
posts would  be beneficial in those  soils  that
show specific  micronutrient deficiencies.

APPROACH:   Solid waste compost  and other
related organic materials  are  added to  soils
known to  be deficient in  specific nutrients.
Plants are  grown on  these soils under care-
fully controlled greenhouse or growth cham-
ber conditions. Growth response to the added
compost is  measured. Initially, a soil showing
zinc deficiency and another showing iron de-
ficiency were used in  these studies.  An in-
crease in plant growth, the nutrient uptake
by the plant and the  nutrient composition of
the  added  organic material  being known,
would indicate that  the hypothesized metal
chelation may be a contributing factor. Period
of incubation,  rate of application,  and other
variables are  being investigated  in order to
consider a variety of experimental parameters.
  The solubilization of micronutrient cations
in waste compost  by the  organic  materials
from  the  decomposing  compost   is  being
studied. Soluble  metal complexes or chelates
in soil extracts are identified  by  using dial-
ysis, chromatography, and infrared absorption
techniques.  Extracted  organic  matter  from
soil-compost  mixtures  is  being  studied  for
stability  constants  of Zn,  Fe, Cu,  and  Mn
complexes.

FINDINGS:   A  series  of  greenhouse  studies
showed that sewage sludge  and garbage com-
post are somewhat beneficial  for  correcting
Zn and Fe  deficiencies in high-pH  soils. Ash-
ing the organic wastes greatly reduced their
effectiveness as Zn and  Fe  fertilizers.  The
organic-matter fraction was beneficial in keep
ing those relatively insoluble nutrients solu-
ble and available for plants.
  Sewage sludge  initially contained  a high
level  of  DTPA-extractable  (available)  Fe.
During  incubation with  soil,  only a  small
but  significant  fraction remained  available.
Increased availability persisted for at least
three cropping cycles. On a dry-weight basis
sewage  sludge was  more  effective  than gar-
bage  compost  in correcting  these  micronu-
trient deficiencies.  N, P,  K, and S were ade-
quately  supplied  so  that growth  response
resulted primarily  from added  Zn or Fe.
  Water-soluble  extracts  of  sewage  sludge,
garbage  composts,  and soils  to which  these
wastes were  incubated were examined to iden-
tify possible chelating agents  responsible  for
the solubilization of metal ions in soil.  Sepa-
rations of the water-soluble extracts on Sepha-
dex G-25 columns gave five molecular-weight
fractions. When  59Fe was added to the  ex-
tracts, it was retained by the higher molec-
ular-weight  fraction. Further  separation and
identification of the  functional  groups  re-
sponsible lor metal  chelation  are in progress,
by use  of chromatographic and infrared  ab-
sorption techniques.
  The study indicates that solid waste  prod-
ucts  such as  garbage composts and  sewage
sludges   are  useful  micronutrient  fertilizers
on soils deficient in these nutrients.  Identi-
fication of soluble metal cheiates arising from
decomposing organic residues is contributing
fundamental information on the beneficial role
of organic matter  in  restoring soil fertility.
                        Conference of Institute for Solid Wastes
                      Mr. Robert D. Bugher
                          Executive Director
         American  Public Works Association
                    Chicago, Illinois  60600
 Grant No. SW 00023-01
 Funds Awarded: $10,000
 Project Period: June 1, 1966 to  Dec. 31, 1966
  These funds  supported,  in  part, the  first
annual  meeting of the  Institute  for Solid
Wastes  (ISW) of the American Public Works
Association   (APWA),  held in Chicago,  Il-
linois, Sept.  10 to  15,  1966.  The Institute
was formed Aug. 29, 1965, within the struc-
                                                                                        13

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ture of the APWA.  The  meeting was held
in conjunction with  the 1966 Public Works
Congress and Equipment Show.
  The funds helped to defray expenses  in-
curred by specially invited representatives of
the  International  Association  of   Public
Cleansing (INTAPUC) in  establishing an in-
ternational  relationship within the  national
framework.  The participation  of experts in
the field of  solid wastes from other countries
enhanced the conference,  which  focused  on
solid waste management research.
  A summary of the Joint  Meeting of the
Executive Councils  of  INTAPUC and ISW
was  published in  the  1966  Proceedings of
the APWA-ISW. The meeting prepared the
groundwork  for  the merger of  INTAPUC
and  the  International  Research  Group for
Refuse  Disposal.  The  two groups merged
into the International  Solid Wastes Associa-
tion  (ISWA) effective Jan. 1, 1970.  ISWA
has as its purpose the development of inter-
national relations and  the  exchange  of  in-
formation on solid wastes and public cleans-
ing The APWA-ISW is  the official national
representative  for  the   United  States  and
Canada  in  the ISWA.   Robert D.  Bugher,
Secretary-Treasurer  of  the APWA-ISW  and
Executive Director of the APWA, is currently
Vice  President of the ISWA.


               PUBLICATIONS
Proceedings; First  Annual Meeting of the Institute for
Solid Wastes, Chicago, Sept. 13-15, 1966. American Public
Works Association. 78 p.
                 National Conference on Packaging Waste Management
                      Dr. George F. Stewart
       Food Protection  and Toxicology Center
              University of California—Davis
                   Davis, California  95616
 Grant No. EC  00324-01
 Funds Awarded: $21,856
 Project Period: Feb. 1, 1969 to Jan. 31, 1970
OBJECTIVES:   To   ascertain  the   changing
nature  and   dimensions of  the  packaging
wastes problem and  to  explore avenues for
solutions  to  this problem,  with due regard
for scientific and technologic aspects, economic
and sociologic factors, legal aspects, and pub-
lic information.

APPROACH:   A conference on packaging and
waste management  was held September 22 to
24, 1969,  at  the  Sheraton-Palace  Hotel,  San
Francisco,  California.  Its  purpose was  to
bring  together  university,  government,  and
industry personnel to examine the magnitude,
complexity,  and growth rate  of  packaging
waste  material,  and  the technical  and  eco-
nomic factors related to its management.  A
complete  proceedings of the conference has
been  published.

                PUBLICATION
First  National  Conference on Packaging Wastes; pro-
ceedings, [San  Francisco,]  September 22-24, 1969. Wash-
ington,  U.S. Government  Printing Office, 1971. 242  p.
(In press.)
14

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                   National  Conference on  Solid  Waste Management
                         Dr. Samuel A. Hart
      Department of Agricultural  Engineering
              University of California—Davis
                   Davis, California   95616
 Grant No. SW 00037-01
 Funds Awarded: $24,069
 Project Period: July 1, 1965 to Dec. 31, 1966
  These funds supported, in part, a National
Conference on Solid Waste Management held
on Apr. 4 and 5, 1966, at Davis, California,
that  explored operations  research and sys-
tems analysis  as  possible tools  in  improving
the approach  to  the  involved  problems  of
solid  waste   management  in  metropolitan
areas.
  Approximately  350  persons  attended the
meeting. Representatives from the U.S. Pub-
lic  Health  Service,  universities,  industry,
governmental agencies,  and  private  institu-
tions  presented  papers that were  published.

               PUBLICATIONS

Solid Wastes Management; Proceedings; National Con-
ference, Davis Campus, April 4—5,  1966, University of
California. 214 p.
                     National Conference on Solid Waste Research
                       Dr.  Ross E. McKinney
             Department of  Civil  Engineering
                       University of Kansas
                   Lawrence,  Kansas  66044
 Grant  No.  EF  00549-01
 Funds  Awarded: $18,478
 Project Period: July 1,  1963 to June 30, 1964
OBJECTIVES:   These funds supported, in part,
a National  Conference  on Solid Waste Re-
search whose purpose was  to stimulate  re-
search in the field. The long-range  aspects of
the  solid waste  management  problem  and
the  urgency  of  working  toward a solution
were recognized.  The conference,   held  for
21/2  days in  December 1963, in Chicago, re-
viewed the solid waste problem in the United
States. Some  36  papers  and summaries were
presented by authorities in the field.
  The conference  covered research  needs in
waste  characterization, waste  collection and
transportation,  and   waste  treatment  and
utilization.  Efforts were directed toward  en-
couraging  young researchers  to  meet  these
needs.
  The budget covered mainly travel and per
diem expenses for program participants and
study section  members. Travel for 30 young
researchers and for 3 foreign scientists, prepa-
ration and printing of the program, stenotype
recording,  and transcription and  publication
of the proceedings were also funded.

               PUBLICATIONS
McKiNNEY, R. E. Proceedings; National  Conference on
Solid Waste  Research, Chicago,  Dec. 1963, University
of Chicago Center  for  Continuing  Education.  Special
Report No. 29. American Public Works Association, 1964.
228  p.
                                                                                         15

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                 National Symposium on Animal  Waste Management
                     Dr. E. Paul Taiganides
      Department of Agricultural Engineering
                      Ohio State University
                    Columbus, Ohio  43212
 Grant No. SW 00026-01
 Funds Awarded: $6,500
 Project Period: Apr. 1,  1966 to Mar. 31, 1967
  These funds supported, in part, a National
Symposium  on  Animal  Waste  Management
at Michigan State University,  May 5 to 1,
1966. The  conference  was  designed to ap-
praise animal waste management needs  and
stimulate research on  problems  in  the  area.
Another objective was  to  provide  a forum
for" teams of scientists, engineers, public health
officials,  and others to  exchange knowledge
on  agricultural waste problems.  More  than
300 persons attended the conference,  includ-
ing a number  of  foreign scientists.

               PUBLICATIONS
Management of Farm Animal Wastes; Proceedings;  Na-
tional Symposium  on Animal Waste Management, East
Lansing, Michigan, May 5—7, 1966,  Kellogg Center foi
Continuing Education, Michigan State University. ASAE
Publication  No. SP-0366. St. Joseph, Mich., American
Society of Agricultural  Engineers. 161 p.
               National Industrial  Solid Waste Management  Conference
                       Dr. H. Nugent Myrick
   Department of Environmental Science  and
                               Engineering
                       University of Houston
                     Houston,  Texas  77004
 Grant  No.  EC 00331-O1
 Funds  Awarded: $29,500
 Project Period: May  1, 1969 to August  31,
    1970
OBJECTIVES:  To develop  and conduct a na-
tional  conference on the management of  in-
dustrial solid wastes. A multisession format
included  coverage  of technical  information
on characterization, collection, processing, and
reuse. Economic aspects and aspects of second-
ary-industry technology were considered.
APPROACH:   The  program was developed by
a national task force committee representing
industrial, professional,  governmental,  and
research interests. The committee worked by
mail, for the most part,  and at any major
technical meeting  attended by  a  significant
number of  the committee  members.  The
chairman made  personal  contacts  with the
pertinent major  professional societies  and
trade associations  to  seek their support or
cooperation.  All  technical  papers  were by
request  and represented  the most  rigorous
evaluation of  the  current  technology  and
state  of the art.  A conference proceedings
will be published.
16

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                  Design of a Water-Disposable Packaging Container
                      Dr. Samuel F. Hulbert
         Division of Interdisciplinary Studies
                         Clemson University
            Clemson,  South Carolina  29631
  Grant No. EC 00033-03
  Funds Awarded: $163,500
  Project Period: Mar. 1,  1968 to  Feb. 28, 1972
OBJECTIVES:   To  develop a  packaging  con-
tainer that, after use, can be  easily processed
to  dissolve in  water.  The  packaging  con-
tainers being  investigated consist of a water-
soluble superstructure with a thin, impervious
coating that resists corrosion  by the environ-
ments commonly encountered in the packing
industry. After  the container  has  been emp-
tied,  it  can  be refilled if  desired,  or  the
coating can  be  broken so  that  the  water-
soluble superstructure can be dissolved.
  Both organic  and inorganic  coatings  are
being tested.  Sodium  silicate glasses, potas-
sium  silicate  glasses, alkali  halides,  peptide
crystals, and sugar derivative crystals are be-
ing investigated as water-soluble  superstruc-
tures. A three-step procedure  for solid waste
disposal  is  envisioned,  as follows:  crushing
or  grinding  followed  by  incineration,  fol-
lowed by dissolution.

APPROACH:   To accomplish these objectives,
kinetic studies  of the  interaction  between
water-soluble  glasses  and  aqueous solutions
are being done.  Kinetic studies of the inter-
action between  "coated" water-soluble glasses
and corroding  media are also being made.
Physical properties such as  tensile  strength,
compressive  strength, flexural strength,  im-
pact strength, fatigue strength, elasticity, and
hardness of the  "coated" water-soluble glasses
before and after the corrosion tests are being
investigated. The inorganic coatings are be-
ing applied by chemical vapor deposition and
ion exchange procedures.  The organic coat-
ings are being applied by use of fluidized bed
procedures. The  effect  of  the coatings and
water-soluble  glasses  upon the  various  bio-
logical systems of laboratory  animals are be-
ing investigated to ensure that the container
materials  developed  are  nondeleterious  to
health.
 FINDINGS:   Soluble silicate glass compositions
 are readily coated by chemical vapor deposi-
 tion processes. Metallic oxides derived  from
 selected organic esters provide excellent coat-
 ing  materials for  soluble glass substrates.
 The high vapor pressure and chemical stabil-
 ity of the mother liquid readily allow coatings
 to be  produced by pyrolysis reactions at the
 heated  substrate  surface.  Titanium  oxide
 coatings are  readily produced  over a  wide
 range  of controlled conditions  such as dep-
 osition  temperature,  time, carrier  gas flow
 rate, reactant vapor concentration,  substrate
 orientation, and  others.  The  coatings pro-
 duced  can  be amorphous or crystalline, de-
 pending upon conditions. These coatings are
 chemically  stable and form a chemical bond
 with a glass substrate. Silicon oxide glass coat-
 ings are produced under  somewhat more  re-
 stricted conditions; however,   the  coatings
 formed likewise  possess excellent properties.
 The problem of residual  stress in the coated
 samples is a greater hazard with SiO2 coatings
 because of generally higher deposition tem-
 peratures and a greater mismatch of thermal
 expansion coefficients.
   The rendering of sodium silicate  glass  in-
 soluble with H2SC>4  in  a displacement  re-
 action  involving participation by the sodium
 ions of the glass is a feasible method of pro-
 ducing  a water-soluble packaging  container.
 The H2SO4 treatment can be used to protect
 complicated shapes because the  procedure  is
 not  critically sensitive to  orientation of the
 substrate and distance from the input vapors.
 The  resulting  glass is transparent  without
 any appreciable  birefringence.  The glass has
 an unusually  high strength because of the
 compressive surface resulting from the chemi-
 cal treatment. The glass fragments are similar
 to "safety"  glass when mechanically ruptured
.and are thus readily dissolved  when broken.
                                                                                         17

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  Sodium silicate glasses  in  the composition
range  1.0 Na2O  • 1.3 SiO2 to 1.0 Na2O   1.6
SiO2  possess adequate strength  and ease  of
workability to be  used as materials of  con-
struction  for containers.
  The engineering feasibility of a water-solu-
ble packaging  container consisting  of  water-
soluble sodium  silicate  glass superstructure
with an inert barrier film deposited  by either
a chemical vapor  displacement reaction  or
pyrolysis  has been demonstrated. The  feasi-
bility of  ultimately applying the technology
derived from this  investigation  to  the solu-
tion of container waste  control problems is
bright; however, these three basic  questions
have to be answered before the  water-soluble
container can become a reality:  (1) What is
the toxicology of the system?  (2) What is the
effect  of  the system  on  water quality?  (3)
What  is the economic evaluation of process-
ing procedures?

                PUBLICATIONS

HULBERT, S. F., and C. C. FAIN. Water disposable glass
container is a subject of  Clemson U. research. Midwest
Engineer, 21(9):10-11, May 1969.
HULBERT, S. F., C. C. FAIN, M.  M. COOPER, D.  T.
BALLENGER,  and C. W. JENNINGS. Improving package dis-
posability. In Proceedings; First National Conference on
Packaging Wastes, San Francisco, Sept. 22-24, 1969. Clem-
son, S.C., Clemson University, p.  147-179.
FAIN, C. C.,  S. F. HULBERT, and M. M. COOPER. Design of
water-disposable  packaging container. ASME Paper No.
69-WA/PID-16.  Presented at  Winter Annual Meeting,
American Society of Mechanical Engineers, Los Angeles.
Nov. 16-20, 1969. 5 p.
                                 A  Study of  Farm Wastes
                      Prof. Stanley A.  Witzel
                    Agricultural Engineering
                     University of Wisconsin
                 Madison, Wisconsin   53706
 Grant  No. Ul 00556-04
 Funds  Awarded:  $138,345
 Project Period: June 1,  1964 to May 31, 1969
OBJECTIVES:   To study  farm  animal wastes
in order to determine quality, physical  char-
acter,  chemical  and  biological composition,
and  the effects  of  animal-housing  practices.
To  evaluate  the  economic  value  of  farm
wastes to agriculture, and any adverse  effect
such wastes may have on public health.

APPROACH:   Wastes  from  dairy  cows  were
collected periodically, weighed, and  analyzed.
Exploratory  analyses of swine and poultry
wastes were  made  and bacteriologic  charac-
teristics of fresh wastes from ruminating ani-
mals, lagoon waste  input, and lagoon micro-
organisms  were investigated.  These  studies
include liquid  manure  wastes being held  in
below-ground  storage tanks  for  removal  to
fields.  In soils, farm wastes receiving different
methods of treatment were compared by di-
rect  field application and  laboratory green-
houses for their value in stabilizing  soil  struc-
ture and  for their contribution to the nutri-
tion of field crops. Sources and amounts  of
pollution of  surface  and  subsurface waters
resulting from various animal waste manage-
ment  and  farming  practices  were studied.
Odor abatement was investigated.
FINDINGS:   Lagoons  appeared to  provide  a
means  of  waste  reduction.  The  final  con-
clusions checked  with the laboratory results
on  this point.  The reasons for less than  100
percent  reduction  became  evident  when
studies on Hgnin indicated the durability of
this type of compound.
  The  fate  of intestinal-pollution types  of
bacteria were  studied and found to follow
the  path of  rapid  reduction during waste
treatment, either  aerobic  or  anaerobic.   Re-
duction  was not,  however, complete  unless
the effluent had been filtered through soil—
the ultimate place of safe disposal for farm
animal waste.
 18

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                  PUBLICATIONS

WlTZEL,  S. A.,  N.  A. JORGENSEN,  R.  F. JOHANNES, H. J.
LARSEN, and C. O. CRAMER. For loose-cow housing: Cold
deep-bedded  pack  vs.  cold  free stalls. Agricultural  En-
gineering, 48 (2):86-88, Feb.  1967.

WITZEL, S, A., E. McCov, and R. LEHNER. Chemical  and
biological reactions  from lagoons  used for cattle. Trans-
actions of the American Society  of Agricultural Engineers,
8(3):449-451, Nov.  20,  1965.

WITZEL, S. A., E. McCov, L. B. POLKOWSKI,  O. J. ATTOF,
and M. S. NICHOLS.  Physical, chemical and bacteriological
properties  of farm  wastes  (bovine species).  In  Manage-
ment  of  Farm  Animal Wastes;  Proceedings;  National
Symposium on Animal Waste Management, East  Lansing,
Michigan, May  5-7, 1966, Kellogg Center for Continuing
Education, Michigan State  University. ASAE Publication
No. SP-0366.  St.  Joseph,  Mich.,  American Society  of
Agricultural Engineers, p. 10.

McCoY,  E. Lagooning of liquid manure  (bovine): Bac-
teriological aspects.  Transactions of the American Society
of Agricultural  Engineers, 10(6):784-785, Nov.-Dec. 1967.

HOADLEY, A. W., E. McCoY, and  G.  A. ROHLICH. Untei-
suchungen ueber Pseudomonas aeruginosa  in  Oberflae-
chengewaessern.  I.  Quellen.  II.  Auftreten und verhalten.
[Investigations  on  Pseudomonas  aeruginosa in  surface
waters. I. Springs.  II.  Occurrence and behavior.] Aichiv
fuer  Hygiene   und Bakteriologie, 152 (4):328-345, Aug.
1968.
HOADLEY, A. W., and E. McCoY.  Some observations on
the ecology of Pseudomonas aeruginosa and its occurrence
in the intestinal  tracts of animals.  Cornell  Veterinarian,
58(3):354-363, July 1968.

MINSHALL, M.,  M. S. NICHOLS,  and S. A. WITZEL. Plant
nutrients in  base flow  of streams  in  southwestern  Wis-
consin.  Water  Resources  Research, 5 (3):706-713,  June
1969.

McCov, E., and W. B. SARLFS. Bacteria in  lakes: Popu-
lation and functional relationships. In  Proceedings; In-
ternational Symposium on  Eutrification: Causes, Conse-
quences, Correctives, National Academy of Sciences, Madi-
son,  Wisconsin, June  11-16,  1967. Washington,  1969.
p. 331-339.

McCoY, E. Removal of pollution  bacteria  from animal
waste  by soil peicolation. ASAE Paper No.  69-430. Pre-
sented  at Annual Meeting,  American Society of Agiicul-
tural Engineers, Lafayette, June 22-25, 1969. 8 p.

HENSLER, R. F., R. J. OLSEN, S. A. WITZEL,  O.  J. ATTOE,
W. H. PAULSON, and R.  F. JOHANNLS. Effect of method
of manure handling on  crop  yields  and runoff losses.
ASAE Paper  No. 69-468. Presented at  Annual  Meeting,
American Society of  Agricultural   Engineers,  Lafayette,
June 22-25, 1969 16 p.

GRAMMS, L.  C.,  L. B.  POLKOWSKI, and S.  A. WIIZEL.
Anaerobic digestion of animal  wastes  (daily bull, poul-
try and swine). ASAE  1'apei  No.  69-462.  Presented  at
Annual  Meeting,  American  Society of  Agricultural Engi-
neers, Lafayette, June 22-25, 1969. 26  p.
                    Disposal of Dairy Cattle Wastes by Aerobic Digestion
                              Dr. Alvin C. Dale
       Department of Agricultural Engineering
                             Purdue  University
                    Lafayette,  Indiana   47907
  Grant No. EC  00244-02
  Funds Awarded:  $113,098
  Project Period:  Jan. 1, 1967 to Dec. 31, 1969
OBJECTIVES:   To   determine  the   chemical
composition,  physical characteristics, and bio-
degradability  of  dairy  cattle  waste and  to
relate this information to  the possible separa-
tion  of various constituents  of the waste  so
as  to render  certain  portions  of  the  waste
more treatable by  aerobic   digestion.  The
composition of dairy waste was related to the
rations of  the cattle and in turn to the treat-
ability.  The  treatability  of  cattle  waste was
determined with regard  to loading rate, tem-
perature,   oxygenation  rate,  and  oxidation
characteristics.

APPROACH:   Waste    characterization   and
treatability studies  were done  for the most
part  in  the laboratory.  Field-acquired sam-
ples were  diluted  and put through a series
of screenings,  sedimentations,  and nitrations
with analysis  of materials  retained  in each
step. Based on these results, methods of pre-
treatment of livestock  waste, including grind-
ing,  were  developed.  Subsequent  to  these
studies  pretreated  waste  in  the  laboratory
was digested aerobically in chambers with the
removal  of sludge as  required.  BOD, COD,
pH,  volatile  solids,  and  total  solids  were
measured as often as necessary while tempera-
ture  was varied to  determine  its effect on
biodegradation  rates.  Concurrently,  quanti-
ties  of wastes produced were determined, and
biological  analysis  was made to  determine
                                                                                                    19

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what  differences in  microorganism  content
of manures result from animals being fed anti-
biotics,  stilbestrol, and other feed additives.

FINDINGS:   A  74-day experiment conducted
at five  different  temperatures on  blended
(ground)  cow  manure  gave  the  following
reductions of volatile solids and CODs.

              Percent reduction   Percent reduction
 Temperature, F   of volatile solids
    40.4
    47.9
    56.2
    64.8
    74.7
45.7
46.7
58.5
71.4
78.6
of COD

 43.3
 57.8
 80.8
 83.7
  A sharp change in the rate of decomposi-
tion of the volatile  solids  and COD seemed
to occur between 45 F and 55 F. The chambers
at higher temperatures, 56.2 F and above, also
had  smaller  solids  concentrations  in  the
settled supernatant liquid.  In an experiment
on the aerobic storage of dairy cattle manure
for  28 days at 4 C and  24 C and four  load-
ing rates, results were as  follows. The holding
temperature  had a  marked effect upon the
degree of change  that took place in the re-
actors. Approximately half as much  of the
constituents  as measured  by  the  volatile
solids,  COD,  and  Kjeldahl  nitrogen  were
lost  in  the 4 C reactor  as were  lost at the
higher 24 C temperature. The data show that
nitrogen was  lost  from practically all the
systems, but the  concentration  of  nitrogen
per gram of volatile  was  higher in the systems
operated at  both  temperatures  than  at the
higher  temperature above,  and  it was the
highest in  the 4 C reactor. This indicates a
lesser reduction of nitrogenous compounds at
the lower temperatures.
  In  regard  to  the percent  removals, the
results  of  all  tests  shows   that  at  24 C the
removals of  volatile solids, COD, and  Kjel-
dahl nitrogen  were  42.3, 53.6, and  43.5 per-
cent,  respectively, and for  the 4  C tests the
removals of  volatile solids, COD, and  Kjel-
dahl nitrogen  were  20.1, 24.5, and  15.9 per-
cent, respectively.
  The  manure,  both  that fresh from the
barnyard  and that stored  under  refrigera-
tion, was odorous and somewhat objectionable
in the  laboratory. • No dbjectionable odors,
however,  were  noted near  the reactors at
either of the two  temperatures. An "earthy"
odor, not unpleasant, was detectable within
a foot of the units.
  Foaming  of the aeration units was a con-
tinuous problem.  The foam was very stable
and  consequently difficult to control. More
foam was produced  by the 4 C units  than
by the 24 C units.
  In another experiment  the  foaming  char-
acteristics of dairy cattle manure were studied
during aerobic digestion. Both foaming  tend-
ency and foaming stability  of raw  manure
slurries were significantly greater (99  percent
confidence)  at 4 C  than at 20 C. A linear
relationship  was found between both foam-
ing tendency and foaming stability and solids
concentration  of manure  slurries  ranging
from 1,000 to 30,000  mg/liter. Foaming  tend-
ency  increased   with  decreasing  fineness
modulus  (particle size distribution). Foam-
ing stability, however, was not affected by the
level of fineness modulus.  Foaming tendency
increased with increasing solids concentration
up  to  15,000  mg/liter but  not  thereafter.
Foaming  stability  was not  affected  by the
solids concentration.  The percent reduction
in total volatile solids obtained in  the  di-
gesters at 20 C varied from 30.0 to 34.9 per-
cent for straight  (nonblended) cow  manure.
  Another phase of the research investigated
the possibility of storing dairy cattle manure
at constant  temperature (20 C)  and  loading
0.02 Ib volatile solids per cu  ft per day in
a reactor with aerobic conditions in  the top
part and anaerobic conditions in the bottom
part of  the reactor. Results  indicated the
following.
  1.  Hydrogen  sulfide was  not produced
during  this  type of storage.
  2. Odors were minimized in aerobic-anaero-
bic storage  of dairy  cattle manure.
  3. There were  reductions of  26.2  percent
in total  solids and of 29 percent  in  volatile
solids when unblended manure was  used.
  4. There were  decreases in  total Kjeldahl
nitrogen and in  COD.
  In an  experiment studying  the effect of
size  of particles  on  decomposition   rate of
volatile solids in  dairy cattle  manure,  there
appeared to be  a definite relation  between
20

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them.  The  finer the particles the greater the
rate of decomposition.
  In an 87-day  experiment  on  the  disposal
of  dairy  cattle manure by  aerated lagoons
and irrigation, the system appeared to be an
excellent  method  for  the disposal of dairy
cattle  wastes. Some of  the  following factors
were evident in  this experiment.
  1.  The  system  is  essentially  odorless   (a
slight  ammonia odor  was  detected  during
loading).
  2. The system provides a  place  to  dispose
of wastes at all times.
  3. A large part of the nutrients is returned
to the land.
  4.  With  proper  operation,  runoff into
streams and ditches is minimized.
  5. Pollutional characteristics of all  wastes
are  greatly lowered.
  6. Costs  of  installation and operation  do
not appear to be excessive.
  7. Relatively small amount  of labor is  re-
quired.
  Irrigation  removed 9 percent of COD, 11
percent of BOD, 14  percent of the volatile
solids, and  23  percent  of the total  solids.
Settling and decomposition by  oxidation re-
moved approximately 60 percent of COD, 70
percent of BOD, 55  percent of the volatile
solids, and 35 percent of the  total solids from
the supernatant.
                PUBLICATIONS

DALE, A. C. Aerobic treatment of animal wastes. ASAE
Paper No. 67-927A. Presented at Winter Meeting, Amer-
ican Society of Agricultural Engineers, Detroit, Dec. 12—
15, 1967. 7 p.

LUDINGTON, D. C.,  A. C. DALE, and D. E.  BLOODCOOD.
Storage  of poultry  manure with  minimum odor. ASAE
Paper No. 67-932.  Presented  at Winter  Meeting, Amer-
ican Society of Agricultural Engineers, Detroit, Dec 12-15,
1967, 19 p.

NYE, J.  C., A. C. DALE,  and D. E. BI.OODOOOD. Effect of
temperature on aerobic decomposition of  dairy waste.
ASAE Paper  No. 69-926. Presented at  Winter Meeting,
American Society of Agricultural Engineers, Chicago, Dec.
9-12, 1969. 10 p.
                         Engineering  Properties of  Farm Wastes
                       Dr. E. Paul Taiganides
       Department of Agricultural Engineering
                       Ohio State University
                     Columbus, Ohio   43210
 Grant  No.  EC 00297-03
 Funds  Awarded:  $50,093
 Project Period: June 1,  1966 to Dec. 31, 1969
OBJECTIVES:   To develop techniques for meas-
uring  and evaluating  some  of  the bio-engi-
neering  properties of  farm wastes useful in
the design of systems for the management of
animal manures  without  creating environ-
mental pollution or public  nuisance.

APPROACH:   Waste  samples from  chickens,
dairy cows,  beef cattle, pigs, and  sheep were
analyzed  to  determine  pollution  potential
parameters.  Standard  tests  on  BOD,  COD,
moisture, and solids  were made. In addition,
data on quantities excreted with  different food
rations were determined. The composition of
gases emanating from manure  pyrolysis  and
also the odor characteristics of  wastes  under
various conditions of storage were determined.
FINDINGS:
  1. Odor nuisance is one of the most critical
problems adversely  affecting  livestock  and
poultry  producers.  By  means of an equili-
bration  sampling  technique, volatiles  from
dairy animal waste  were concentrated into a
form suitable for gas chromatographic analy-
sis.  An odor signature, the gas chromatogram
with an  organoleptic evaluation indicated for
odorous  peaks,  was obtained  for dairy waste
decomposing anaerobically. Compounds  ten-
tatively identified as contributing to the odor
were hydrogen  sulfide, methanethiol, methyl
sulfide,  ethyl   sulfide,  propyl  acetate,  and
n-butyl acetate.
  2. Agricultural land is  the  best alternative
for the disposal of  animal wastes.  By use of
                                                                                          21

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a  systems  analysis  approach, a  scheduling
model was developed for studying long-term
scheduling  decisions  for  removing  animal
waste from storage and  spreading it on agri-
cultural land. The  maximum quantity  that
can be  disposed,  in  each time period, is  con-
strained  by  storage  capacity,  quantity  of
waste generated,  and  land area available for
spreading. An  air quality model was devel-
oped for  evaluating  the  odor  nuisance  po-
tential  of animal wastes  as  a constraint on
land  spreading  operations.   The  principal
parameters affecting downwind ground level
concentration of odors  are  emission  rate,
wind speed,  diffusion coefficient,  and turbu-
lence index.
  3. A  menace from  noxious gases exists in
animal  confinement units. It was determined
that under normal operating conditions gases
in confined animal houses do not reach toxic
or lethal levels.  Toxic level  may  be reached
during  failure  of the forced  ventilation  sys-
tem or  as a  result  of mismanagement  prac-
tices, such as agitating liquid  manure storage
under the building.
  4. Combustion of animal manures is a pos-
sible  unit operation in  a waste management
system.  Animal wastes were pyrolyzed, heated
to 800 C out  of contact with air. Gases, water,
and organic  liquids were evolved, leaving  a
clear residue. The  gases were analyzed  for
the percentage of CO2,  CO,  H2, illuminants
(unsaturated   hydrocarbon),   methane,  and
ethane.
  5.  In the  design  of  biological  treatment
units, values on  the  oxygen  demand of  the
waste are  essential.  In  the determination of
the  oxygen   demand  parameters of  animal
wastes,  seeding,  temperature, method  of de-
termination,  and type of waste have a signifi-
cant effect. Storage  of samples at below  2 C
does not have a significant effect.
  6. In  the  design of waste management  sys-
tems, a  knowledge of the quantities  of waste
excreted by animals is< essential.  The quanti-
ties of the  total excrement from animals are
significantly affected  by the feed, the weight
of the animal, and the type  of the animal.
The total daily manure excrement varied from
around 15 percent of body weight when cows
were  fed  silage to 6 percent when they were
fed corn and grass silage. Cow manure ranged
from 13 to 53 percent  of the  feed intake per
day.


                PUBLICATIONS

TAIGANIDES, E. P. Waste  problem recognized;  research
help  on  manure disposal  on the way. National  Hog
Farmer, ll(7):22-23, July 1966.
TAICANIDES, E. P.  The animal waste disposal  problem. In
N. C. Brody, cd.  Agriculture and the quality of our en-
vironment.  Washington,  American Association  for the
Advancement of Science, 1967. p.  385-394.
TAICANIDES, E.  P., and T. E. HAZEN. Properties of farm
animal excreta. Transactions of the American Society of
Agricultural Engineers, 9 (3):374-376, 1966.
TAICANIDES, E.  P. Modem methods of animal waste dis-
posal. In Proceedings; 27th Annual Meeting, Nutritional
Council of American Feed Manufacturers  Association,
Chicago, May 22, 1967. p.  21-22.
TAIGANIDES, E. P. The battle of the forgotten end.  ASAE
Paper No. 67—925. Presented at Winter Meeting, Ameri-
can Society of Agricultural Engineers, Detroit, Dec. 12-
15, 1967.
TAIGANIDES, E. P.  Farm-waste management in Europe and
India. Agricultural Engineering, 48 (12):710-713, Dec. 1967.
WHITE, R. K. Gas chromatographic analysis of odors from
dairy animal wastes. Ph. D. Thesis, Ohio State University,
1969. 143 p.
TAIGANIDES, E. P. Mission  impossible:  dispose animal
wastes. Presented at 24th Annual Purdue Industrial Waste
Conference, Purdue University, Lafayette, May 6-8, 1969.
13 P.
WHITE,  R.  K., and  E. P.  TAIGANIDES.  Malodors from
dairy cattle wastes.  ASAE Paper No. 69-425. Presented
at Annual  Meeting, American  Society  of  Agricultural
Engineers, Lafayette,  June 22-25,  1969. 8 p.
TAICANIDES, E. P., and R.  K. WHITE. The  menace of
noxious gases in  animal confinement  units. Transactions
of the American Society of Agricultural Engineers,  12(3):
359-362, 367, May-June 1969.
22

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                  Handling, Treatment, and Disposal of Animal Wastes
                       Dr.  Thamon E. Hazen
             Agricultural Experiment  Station
                       Iowa State University
                        Ames,  Iowa  50010
 Grant No. SW 00040-03
 Funds Awarded: $74,019
 Project Period: June 1, 1963 to May 31, 1966
OBJECTIVES:   To  determine  the  physical,
chemical, and bacteriologic properties of hog
wastes and  to  test methods for the manage-
ment, treatment, and  disposal of these wastes
in order to reduce any health hazards or po-
tential  water pollution.  Wastes from  other
farm  animals were also  studied but  in less
detail.

APPROACH:   Lagoons  and the resulting  efflu-
ent  received the  greatest  attention under
various liquid and solid waste loadings. An-
aerobic digesters and an oxidation ditch  were
also studied. Properties of raw  manures and
treated effluents were  evaluated for total and
volatile solids; specific weight;  BOD; COD;
nitrogen, phosphorus, and  potash  content;
toxic substances; and other characteristics.

FINDINGS:  An anaerobic lagoon loaded at a
rate of  3.5 to 5 Ib of volatile solids per 1,000
cu ft  provided satisfactory  preliminary treat-
ment to liquid  swine manure. Total solids
were  reduced by 75  to 80 percent;  volatile
solids, 85 to 90;  COD, 85 to 90; BOD, 60 to
70; and total nitrogen, 45  to 50. The pH of
this lagoon remained at 7.1 or above.  Red-
pigmented bacteria became established  each
summer, and this tended to reduce hydrogen
sulfide  odors. In spite  of  the  pollutant  re-
moval,  the effluent was unsuitable  for dis-
charge  to a receiving stream.
  A series of experimental anaerobic lagoons
was used to determine the desirability of  deep
(10 ft) lagoons.  To  avoid  occasional  mal-
functions,  a swine  manure  loading rate of
5  Ib  of volatile solids  per 1,000 cu ft was
established. For swine wastes, a lagoon design
criterion  of  1.42 cu ft/lb  of animal  weight
was proposed.
  A heated-stirred anaerobic digester being
used to treat swine manure, loadings  of 20 Ib
of volatile solids per  1,000 cu  ft were found
operable.  At  higher  loading  rates, copper
appeared to inhibit digestion.  Gas, 60  per-
cent methane,  was  produced at rates of 7.8 to
10.3 cu ft/lb of volatile  solids. The digested
solids  were  not attractive to flies and  were
free of offensive odors.
  A mathematical  model was  derived  and
verified  to predict the  performance of  an
extended aeration  plant treating lagoon  efflu-
ent. BOD removal efficiencies in excess of 80
percent  were  obtained.  The parameters of
importance in  determining treatment efficien-
cies were  mixed-liquor   volatile  suspended
solids,  detention time, and influent quality.
  In an  evaluation of  an  oxidation  ditch
rotor at immersions of 6, 9, and  12 in.  and
speeds of  60 and  100 rpm,  oxygen transfer
rates of 2.3 to 17  Ib/hr  and 3.6 to  4.4 Ib of
oxygen per kw-hr  were  measured.
  An exploratory  study  in  which anaerobic
lagoon  effluent was applied  to  soil columns
indicated the  necessity for alternate periods
of wastewater application and nonapplication
to  maintain acceptable   permeability  rates.
Soil temperature was important in determin-
ing the rate of recovery  of soil permeability.


                PUBLICATIONS

TAICANIDES, E. P., E. R. BAUMANN,  H. P.  JOHNSON, and
T. E. HAZEN. Anaerobic digestion of hog wastes. Journal
of Agricultural Engineering Research  (London),  8(4):
327, 1963.
TAIGANIDES, E.  P., E.  R. BAUMANN, and  T. E.  HAZEN.
Sludge digestion of farm animal wastes. Journal  Paper
No.  J-4661, Iowa  Agricultural and Home Economics Ex-
periment Station,  Ames, Iowa.  Project No.  1433.  Pub-
lished, Compost Science, 4(2):26, Summer 1963.
TAIGANIDES, E. P.  Agricultural  solid wastes. In Proceed-
ings; National Conference on Solid Waste Research, Chi-
cago, Dec. 1963, University of  Chicago Center for Con-
tinuing  Education. Special  Report No.  29. American
Public Works Association, 1964. p. 39.
                                                                                          23

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TAIGANIDES, E. P., T. E. HAZEN, E.  R.  BAUMANN, and
H. P. JOHNSON. Properties and  pumping characteristics
of hog wastes. Transactions of the American Society of
Agricultural Engineers, 7 (2): 123,  1964.

TAIGANIDES, E. P. Disposal of animal wastes. In Proceed-
ings of the Nineteenth Industrial Waste Conference, Pait
One,  Purdue  University  and Indiana State Board of
Health, Lafayette, Indiana, May 5-7, 1964. In Engineering
Bulletin of Purdue  University, Engineering Extension
Series No.  117, 49(la):281-290, Jan. 1965.

TAIGANIDES, E.  P. Disposal  of  animal  wastes. Journal
Paper No. J-4876, Iowa Agricultural and  Home  Eco-
nomics Experiment Station, Ames, Iowa, Project No. 1433,
1964.

TAIGANIDES, E. P. Theoretical considerations of anaerobic
lagoons for poultry  wastes. Journal  Paper  No. J-4889,
Iowa  Agricultural  and   Home  Economics  Experiment
Station, Ames, Iowa. Project  No. 1433, 1964. Published,
Proceedings;  Second   National Symposium  on Poultry
Industry Waste Management,  Lincoln, May  19-20, 1964,
University of  Nebraska Center for Continuing Education.
p. 251.
TAIGANIDES, E. P., and -T.  E. HAZEN. Piopeities of farm
animal  excreta.  Transactions of the American Society  of
Agricultural Engineers, 9(3):374-376, 1966.

WILLRICH, T. L. Primary  treatment of swine wastes  by
lagooning.  In Management of  Farm  Animal Wastes;
Proceedings;  National Symposium  on  Animal Waste
Management, East  Lansing, Michigan, May  5-7, 1966,
Kellogg Center for Continuing Education, Michigan State
University.  ASAE Publication No. SP-0366. St. Joseph,
Mich., American  Society of Agricultural Engineers, p. 70.

WALLIZE, J. The story of a 'model'; swine in confinement.
Iowa Farm Science, 22(1):3, July  1967.

MINER,  J. R., and T. E. HAZEN. Alternatives to oxidation
ditches  under  slotted floors.  In  Proceedings;  Tenth
National Pork Industry Conference,  Lincoln, Nebr., Nov.
9,  1967.
TAIGANIDES, E. P. Anaerobic digestion of poultry manure.
World's Poultry Science Journal, 19(4):252-261, Oct.-Dec.
1963.
                      Identification of  Odors in  Feedlot  Operations
                        Dr. Edgar R. Stephens
      Statewide Air Pollution Research  Center
           University of California—Riverside
                  Riverside, California   92502
  Grant No.  Ul 00531-02
  Funds Awarded: $49,329
  Project Period: Feb. 1, 1967 to Apr.  30,  1969
OBJECTIVES:   To identify the odors associated
with  confinement  livestock  operations.  To
provide the analytical means for assessing the
magnitude  and  possible effect  of the  odors
on a community and for evaluating the effec-
tiveness  of  modifying  feedlot  practices  to
reduce odors.
APPROACH:   Gas chromatography with flame
ionization or electron capture detection  was
the principal method used. Since the intensity
of  the odors from a  real feedlot is heavily
dependent on weather and  the state  of the
feedlot, most of the analytical development
was carried  out on  laboratory  mixtures. An
odor threshold test equipment was assembled
and used  to  assess the intensity of odors.


FINDINGS:   Trimethylamine   is  a  principal
substituent  in cattle feedlot  atmospheres in
concentrations well  above its odor threshold
of 0.6 ppb. Several experiments, including a
simple  odor  comparison  test,  verified  this.
Limited results  show  that  ethylamine  or
methylamine,  propylamine,  and butylamine
are also present in concentrations above  their
odor thresholds.  Ammonia and perhaps hy-
drogen sulfide or a mercaptan are present but
in  concentrations below  their odor  thresh-
olds. Time did not permit a thorough analy-
sis  of fatty acids  or  alcohols.  Amines  proved
especially difficult to handle in trace quanti-
ties because of  their  ready  adsorption  onto
surfaces, but useful chromatographic methods
were finally developed.  Many  techniques for
sample  collection and additional  techniques
such as  paper chromatography were tested
briefly.
   Future  work  should include research in
this area since acids are a  product of  decom-
posing protein as are  amines.  More informa-
tion concerning odor thresholds of  these  odor-
ants  is also needed.
 24

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                    Livestock Waste  Management  and  Sanitation
                         Dr.  Donald L. Day
      Department  of Agricultural Engineering
                       University of Illinois
                    Urbana, Illinois  61801
 Grant No. EC 00245-03
 Funds Awarded: $96,894
 Project Period: Sept. 1,  1966 to Feb. 28, 1970
OBJECTIVES:  To  refine  knowledge  of  the
physical, chemical, and biological properties
of livestock wastes for the  development  of
methods of waste treatment and management
that  meet the requirements of low labor and
odor  abatement,  and pollution abatement.
The project was principally  concerned with
swine waste management, but  cattle  wastes
were investigated  to a limited  extent.

APPROACH:  Primarily, field studies were con-
ducted  on the  University of  Illinois swine
and  beef  farms  equipped  with liquid waste
facilities,  oxidation  ditches,  sandbed  filters,
and a series of lagoons. The buildings housing
the  hogs  and beef cattle  have self-cleaning
slotted  floors with liquid  manure  collection
gutters  beneath  the floor.  Laboratory studies
supplemented the  field studies when required.
  The studies considered aspects of chemical
treatment of liquid manure  and an  aerobic
treatment  process to suppress  objectionable
gases and  odors. In the chemical  treatment
study, the type and amount of  treating mate-
rials  needed,  and the  management  proce-
dures for  removing  and  using  these solids
were studied. In the aerobic  biological study,
design and operating criteria  were developed.
These included  oxygeuation  characteristics of
cage rotors, allowable concentrations of solids
in the liquid, BOD loading rates, liquid veloc-
ity requirements to prevent settling, and ulti-
mate disposal  methods of  surplus water and
solids.

FINDINGS:  The main chemicals studied for
odor control were chlorine  and lime.  They
were used  to prevent the otherwise untreated
anaerobic state of liquid manure beneath the
animals and the resulting  objectionable gases
and odors. The  chlorine acted as a bactericide
and was very  effective, even  in amounts less
than the  organic  matter's chlorine demand.
  The lime acted to control  the  pH  in  the
9 to 11 range that was considered too high
for  anaerobic  bacterial  action.  This  also
worked, but the resulting release of ammonia
at the high pH levels was very objectionable
in the buildings. However, the costs of chem-
ical  treatment approached or  exceeded esti-
mated  costs of biological treatment, and  the
organic matter was practically unchanged as
a potential water  pollutant. Thus, the chemi-
cal treatment method was abandoned in favor
of aerobic biological treatment since the latter
method held promise not only for odor con-
trol  but also  for significant reductions in  the
BOD.
  The aerobic  approach resulted in a live-
stock waste  management  system  that very
nearly satisfies the criteria  of  low labor cost,
low  odor,  prevention  of  stream pollution,
simplicity of operation, and economic feasi-
bility.  The system consists of an  oxidation
ditch beneath self-cleaning slotted floors  in
a  confinement  livestock  building.   Mixed
liquor from  the  oxidation  ditch flows  by
gravity to a nonoverflow aerobic lagoon (oxi-
dation  pond or  aerated  lagoon)  having  a
fluctuating depth.  Fields  can  be irrigated
by surplus water  and solids from  the lagoon
at a time that is  convenient to the operator.
This results  in a system that is very low in
labor cost and in odors from animal to field.
  The  in-the-building  oxidation  ditch  is  a
completely mixed aerobic  method having  a
long detention time (approximately 50 days).
It is a  modified  form  of the  odorless "Pas-
veer" oxidation  ditch  treatment  plant  that
was  developed in the Netherlands.
  Results of this project, both in laboratory
and  field  trials,  have  shown  the  operating
criteria of the in-the-building  oxidation ditch
to be as follows.
   1. A ditch liquid volume  of 30 cu ft/lb
of daily BOD5.  Note,  the loading BOD5  is
                                                                                       25

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in a very concentrated form  (30,000 to 50,000
mg/liter instead of 300 to 500 mg/liter as  in
municipal oxidation  ditches).
   2.  The  liquid  depth  is  shallow,  usually
less  than 2 ft, to keep the solids suspended.
   3. The aeration rotor should have an oxy-
genation capacity  (as measured in clean water
at standard conditions) twice that of the daily
BOD5 loading.
   After  coming  to  equilibrium, the  ditch
mixed-liquor BOD5  will  typically be  3,000
to 5,000 mg/liter, resulting in a 90  percent
reduction of the BOD5. Moreover, total vola-
tile  solids are reduced  by about 50 percent.
However,  the effluent, even  if  the settleable
solids were  removed from  the  supernatant,
is not  suitable  for  direct  discharge  into  a
stream because of the color  (reddish  brown),
the  mineral  content,  and even the BOD. This
is the  reason  for the nonoverflow  aerobic
lagoon  and  the irrigation  system.
   Several types of cage rotors  were tested  in
clean  water for oxygenation  output. A typical
value was  1.6 Ib O2/hr/ft at 6-in. rotor blade
immersion and 100 rpm.  Moreover, a related
laboratory study  resulted  in establishing the
amount of aeration required for given levels
of odor production. The aeration rates ranged
from  excessive for the BOD down to no air
in five  steps.
   Many livestock  producers are adopting this
waste treatment system, and at least two com-
panies are manufacturing aeration rotors spe-
cifically for  livestock oxidation  ditches. The
method does,  of  course, have  inherent  costs,
the  greatest being the power cost of operating
the  rotor. This may, however, be an  attrac-
tive alternative to the producer  faced with
odor  nuisance or complaints  about  stream
pollution.


                 PUBLICATIONS
 HAMMOND, W. C., D. L. DAY, and E. L. HANSEN. Can
 lime and chlorine suppress odors in liquid hog manure?
 Agricultural  Engineering, 49 (6):340-343, June 1968.
DAY, D. L.,  and J.  C.  CONVERSE. Oxidation  ditch for
swine  waste.  In  Engineering Foundation Research Con-
ference, Solid Waste Research and Development,  Univer-
sity School,  Milwaukee, July  24-28, 1967.  Conference
Preprint No.  E—5. 3 p.

DAY, D. L. Current status of the oxidation ditch; sum-
mary of United  States and European research. Presented
at  Tenth National  Pork Industry Conference, Lincoln,
Nebraska, Nov.  9, 1967, 8 p.

JONES, D. D., B. A. JONES, JR.,  and D. L.  DAY.  Aerobic
digestion of cattJe waste. Transactions of the American
Society of  Agricultural  Engineers, 11(6):757—761, Nov.—
Dec. 1968.

DALE,  A. C., and D. L. DAY. Some aerobic decomposition
properties  of dairy-cattle manure.  Transactions  of the
American Society of Agricultural Engineers, 10(4):546-548,
1967.

DAY, D. L. Oxidation ditches combine well with slotted-
floor hog setups. Prairie Farmer, 140(3):58, Feb.  3, 1968.

DAY, D. L., J. C. CONVERSE, and D. D. JONES. Rotor aera-
tion of swine wastes. Illinois Research, 10(2):16-17, Spring
1968.

JONES, D. D., B. A. JONES, JR., and D. L.  DAY.  Aerobic
digestion of cattle waste. Transactions  of  the American
Society of  Agricultural  Engineers, 11 (6):757-761, Nov.-
Dec. 1968.

JONES,  D. D., B. A. JONES,  JR., and D. L. DAY.  Aerobic
digestion  of cattle  wastes.  Illinois Research,  10(3):8,
Summer 1968.

DAY, D. L., D. D. JONES, and J.  C. CONVERSE. Field testing
the oxidation ditch for  swine waste. Presented at Engi-
neering Foundation Research Conference, Solid Waste Re-
search and Development, II,  Beaver Dam, Wis. July 22—26,
1968.  Conference Preprint No. E-4.

DAY,  D. L. Oxidation ditches  for waste disposal. Inter-
national Journal of Farm Building Research, 3:2-7,  Dec.
1968.

JONES, D. D., D.  L. DAY, and J.  C. CONVERSE. Oxygenation
capacities of  oxidation ditch rotors for confinement  live-
stock buildings.  Presented at 24th Annual Purdue Indus
trial Waste Conference, Purdue University, Lafayette, May
6-8, 1969. 15 p.

MUEHLING, A. J ,  and  D. L. DAY.  State  regulation  of
lagoons. Prairie  Farmer, 144(10): 14, May 17,  1969.

DAY,  D. L., D.  D. JONES, J. C. CONVERSE,  A.  H.  JENSEN,
and E. L. HANSEN. Oxidation  ditch treatment of swine
wastes. ASAE Paper No.  69-924.  Presented  at  Winter
Meeting,  American  Society  of  Agricultural  Engineers,
Chicago, Dec. 9-12, 1969. 15 p.

JONES, D. D., D. L. DAY, and U. S. GARRIOUS. Oxidation
ditch  in a confinement  beef building.  ASAE  Paper No.
69—925. Presented at Winter Meeting,  American  Society
of Agricultural  Engineers, Chicago, Dec. 9-12,  1969. 10 p.
 26

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                      Microbiological Stabilization of Animal Wastes
                        Dr.  Edward C. Berry
                 Department of Bacteriology
                  South Dakota State College
            Brookings,  South Dakota  57006
 Grant  No. Ul 00519-03
 Funds  Awarded:  $67,355
 Project Period: June 1,  1964 to Nov. 30, 1967
OBJECTIVES:   To study  the stabilization of
livestock wastes  by microbial means  and to
determine  the physical, chemical, and micro-
biological  characteristics of these wastes,  and
the changes occurring to the point of stabili-
zation. To obtain information that will give
engineers  design  criteria for the kinds  and
sizes of processing equipment needed  to con-
vert this material into  a less unsanitary state.
APPROACH:   Measured  quantities of  animal
excreta were placed  in  a stainless steel  di-
gester  tank. Their stabilization  was observed
while  oxygen supply, pH, temperature,  and
amounts of water were varied. The microbial
flora were also  studied in order to improve
the stabilization rate. The biochemical oxygen
demand (BOD) was determined at the start
and end of the biox process to give a measure
of the  changes made and the degree of stabi-
lization. The various  gases  produced, CH4,
CO2, NH3,  H2,  and  H2S,  were collected  and
measured.
FINDINGS:  Anaerobic  and  aerobic  microor-
ganisms  are necessary to reduce the BOD of
animal waste to acceptable levels.  Studies are
underway  to  determine the  organisms  and
their enzymes  responsible  for  production of
hydrogen  sulfide  and  thio-alcohol  during
treatment of animal waste. Strength of animal
waste has been related to  human wastes.

                PUBLICATIONS

BULLERMAN, L. B., and E. C. BERRY. Use of cheese whey
for vitamin B,2  production.  II. Cobalt, precursor, and
aeration levels. Applied  Microbiology, 14(3):356, May
1966.
BULLERMAN, L. B., and E. C. BI.RRY. Use of cheese whey
for vitamin B12 production. III. Growth studies  and dry-
weight activity. Applied  Microbiology, 14(3):358, May
1966.
BERRY, E.  C.  Requirements for microbial reduction  of
farm  animal wastes. In Management of  Farm Animal
Wastes; Proceedings;  National Sympdsium  on Animal
Waste Management, East Lansing, Michigan, May 5—7,
1966,  Kellogg Center for Continuing Education,  Michigan
State  University,  ASAE  Publication   No. SP-0366. St.
Joseph,  Mich.,  American  Society  of  Agricultural En-
gineers, p.  56—58.
                     Poultry Manure Disposal  by Plow Furrow Cover
                    Professor Harry E. Besley
  Bureau  of  Conservation and Environmental
                                    Science
               Rutgers—The State University
         New Brunswick, New Jersey  08903
 Grant  No.  EC 00254-03
 Funds  Awarded: $192,570
 Project Period: Dec. 1, 1966 to Mar. 31, 1970
OBJECTIVES:   To  develop  equipment  and
techniques for  disposing  of  poultry manure
in  soil  by   the  plow-furrow-cover   (PFC)
method and to determine the amounts, fre-
quency of application, and length of time that
poultry manure may be  so disposed of with-
out undesirable effects. To measure the chemi-
cal, physical, and biological changes occurring
in the soils used and to determine the pollu-
tional effects on the ground water.
                                                                                          27

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APPROACH:  Equipment  was  developed  to
permit the depositing of  poultry manure  in
the soil by the PFC method. Poultry manure
then applied  to various experimental  plots.
Numerous hybrid  sudan  grass  crops  were
grown in the  second  year. Lysimeters were
used  to  collect percolation  water  at  a 4-ft
depth for analysis. In  addition to the  perco-
lation water collected  by  the lysimeters, soil
samples  were   taken  at various  times  from
three intermediate depths, and the extract was
analyzed to determine the rate of percolation
of contaminants.
   Laboratory  studies  determined the  maxi-
mum concentration  of chicken manure that
the  soil  could decompose  without adverse
effects.  A  manure loading  was applied  to
the  soil,  and  after a given  percentage  of
the manure had decomposed, another loading
of equal magnitude was applied, and  so on,
until the relative merits of the different load-
ing regimes could  be assessed. Selected soil
characteristics  such as organic matter content,
texture, pH, fertility, exchange capacity, and
water-holding  capacity were evaluated  before
and after each experiment  to  provide  infor-
mation on the changes occurring in the soils.

FINDINGS:  To  apply wastes  by  the   PFC
method,  various  components  of equipment
were  developed and used in this project.  In
this method  of waste disposal, slurries and
semisolid wastes  are  incorporated into  the
aerobic layer of the soil in  a relatively odor-
free manner that does not  attract flies and
other pests. It involves depositing  the  waste
in a 6-  to 8-in.-deep plowed furrow and im-
mediately covering it. The covering operation
provides  the  next  furrow  into which  the
waste is deposited.
   Poultry manure was PFC applied into test
plots of  Freehold loamy sand  (B horizon of
20 percent  clay) in  amounts equivalent  to
0, 15, 30, and  45 tons of  dry solids per acre.
This is  only  half  of  the stated application
rate. An initial application of 0, 15, 30, and
45 tons was planned  for  the surface during
winter months; however,  because of the dan-
ger of stream  pollution from surface runoff,
this application was not made. Because of the
slow downward movement of the elements in
the  soil,  crops were  not planted,  and  the
variable  of  plant takeup1 in observing  the
rate of downward movement of elements was
thereby avoided. Soil water was sampled with
suction  lysimeters, and soil samples were col-
lected. Samples collected 131 days and  17 in.
of rainfall after the  PFC  application showed
a downward movement of Ca, Cl, K, Mg, Na,
NO3 +NO2~N, and  SO4 to a depth of  36 in.
Samples collected 391  days and 50  in.  of
rainfall after  the PFC  application  showed
considerable  increase in  element concentra-
tion at the  36- and 48-in.  depths. The  dis-
solved nitrogen  (N)  in the soil water, totaled
for the  soil  depth from 9 to 48  in.,  was 20,
186, 526, and 1,026  Ib/acre for the four ap-
plication rates of 0, 15, 30, and  45  tons of
dry solids per acre.  The maximum  concen-
tration  was  700 ppm nitrogen (N). Disposal
of these large amounts of poultry manure in
soil caused large increases in the concentra-
tions of elements in  the soil water down to a
depth of 48 in.
   The  pollution potential  to  ground  water
was also investigated.  Percolation water  was
collected 48  in. below  ground  surface  by
means  of zero-tension  lysimeters. Data  for
fecal  coliform  and total   organic  carbon
(TOG)  were  obtained in  addition to  the
elements previously listed. After  7  months
there was  no significant  difference in  the
TOG concentrations for the several  applica-
tion rates  (loadings).  The lack  of  positive
fecal coliform tests with the relatively small
nitrate  and  sulfate  concentrations tend  to
indicate no  detrimental effects to  the ground
water  7 months after the  PFC  application.
However, 12 to 15 months  after the  applica-
tion some very  large  nitrate,  sulfate, and
TOC concentrations were  measured  in  the
ground water. This  corresponds  to the large
increase in  the  concentration  of  elements
noted in the  soil water to a depth of  48  in.
   Laboratory experiments were conducted to
evaluate the effect  of variables  on the rate
of  decomposition   (as  measured  by  CO2
evolution)  of excreta  mixed  with soil. The
absolute amount of  CO2 evolved was greatest
at the higher loadings (up to soil:excreta=
1:1), but the percent decomposition of  added
excreta was  greatest at the  lower loadings
(down  to  10:1).  Temperature  (4, 12,  and
20 C) had little effect on  the rates of CO2
 28

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evolution at the lower" loading regimens. Suc-
cessive  increments  of  excreta  decomposed
about as rapidly as  the  original addition.  At
low  loadings,  soil  texture  had  little  effect,
but  at  higher  loadings decomposition  was
fastest in the lighter soils tested. A salt con-
centration equivalent to about eight excreta
applications at the low rate  inhibited decom-
position only slightly.
  Any  method of  disposing  of  chicken ex-
creta should take into  account the possible
presence of substantial numbers  of  Salmon-
ellae, which are human  pathogens.  Approxi-
mately 30 percent of the excreta samples ob-
tained from commercial farms  for  these de-
composition studies contained Salmonella.

                PUBLICATIONS

KRAFT, D. J.,  C.  OLECHOWSKI-GERHARDT,  J.  BERKOWITZ,
and M. S. FINSTFIN. Salmonella in wastes produced  at
commercial poultry farms.  Applied  Microbiology, 18(5):
703-707, Nov.  1969.
                  Sanitary  Engineering Applied to  Livestock Manures
                         Dr. Samuel A. Hart
      Department of Agricultural Engineering
               University of California—Davis
                   Davis, California  95616
 Grant  No. EF 00265-04
 Funds  Awarded:  $59,875
 Project Period: Sept. 1,  1961 to Aug. 31, 1965
OBJECTIVES:   To develop sanitary and effec-
tive  methods of processing  and disposing of
the manure  produced on concentrated live-
stock farms  such as  dairies,  beef feed lots,
and  poultry  farms.  To  develop improved
methods of  collecting and  transporting  ma-
nure from the point at which it is defecated
by the animal.

APPROACH:   Extensive  laboratory and  pilot
plant operations of various  processing  and
stabilization    techniques—solids   digestion,
manure lagoons, algae ponds, composting, and
drying—were conducted to develop  manure
management  methods feasible  at the  farm
level. Ultimate disposal  techniques and out-
lets were evaluated. The overall research con-
cept was that  the most feasible end  disposal
would be agricultural land.

FINDINGS:   From the tanner's viewpoint, la-
goons can be made to work,  but underground
water  pollution is  a definite hazard, odors
are likely, and costs are not  as low as farmers
desire.
  Research   was also done  on digestion of
manure, and its limitations of cost and ulti-
mate disposal of  the digested sludge  were
determined.  Composting as a method of ma-
nure  processing was  found  to  be less than
satisfactory at the farm level.
  The greatest  potential for proper manage-
ment of most livestock manure appears to be
via variations in  the  natural  drying process.
The  summer-arid climate  of California can
be taken advantage of, and systems of storing
manure  during the winter are possible. Dry-
ing was accomplished by "thin spreading" or
by  mechanically  tilling and  agitating foot-
deep  beds of manure.
  The results of  this  research have been ap-
plied by California farmers,  and the state of
wastes management practices  has benefited
from  the research effort.

                PUBLICATIONS

HART,  S. A. Digestion tests o£ livestock wastes. Journal
of Water Pollution Control Federation, 35(6):748, June
1963.
HART,  S. A.  Fowl  fecal facts. World's Poultiy Science
Journal, 19(4):262, Oct._Dcc. 1963.
OSTRANDER, C. E., and  S. A.  HARI. Degradation of manuie
collected in water under chickens. Poultry  Science, 43(5):
1H4, Sept. 1964.
HART,  S. A. Thin spreading of sluriied manures. Trans-
actions American Society of Agricultural Engineers, 7(1):
22, 1964.
                                                                                          29

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HART,  S. A., and W. C. FAIRBANK. Disposal of perished
poultry. In Proceedings, Second National Symposium on
Poultry Industry Waste Management, Lincoln, May  19-
20, 1964, University of Nebraska Center for Continuing
Education, p. 213.

HART,  S. A., and M. E. TURNER. Poultry manure lagoons.
In Proceedings, Second National Symposium on Poultry
Industry Waste Management, Lincoln,  May 19—20, 1964,
University  of Nebraska Center for Continuing Education.

HART,  S. A., and M. E.  TURNER. Lagoons for livestock
manure. Journal of  Water Pollution Control Federation,
37(11): 1578, Nov. 1965.

HART,  S. A., and C. G. GOLUEKE.  Producing algae in
lagoons. Transactions• of the'American Society  of Agri-
cultural Engineers, 8:122, Nov.  1965.

HART,  S. A., and M. E. TURNER. The  design  of waste
stabilization  ponds  for the treatment  of agricultural
wastes. Paper presented at lecture series on Advances in
Water  Quality Improvement, Austin, Apr. 4-7, 1966. The
University of Texas.

HART,  S. A., J.  A.  MOORE, and W. F.  HALE.  Pumping
manure slurries. In Management of Farm Animal Wastes;
Proceedings;  National  Symposium  on  Animal  Waste
Management, East Lansing, Michigan,  May 5—7,  1966,
Kellogg  Center  for Continuing Education,   Michigan
State  University. ASAE  Publication No.  SP-0366.  St.
Joseph, Mich., American Society  of Agricultural Engineers.
p. 34.
                     A Recirculating Waste System  for Swine  Units
                         Dr. J. Ronald  Miner
      Department of Agricultural Engineering
                       Iowa State University
                         Ames,  Iowa  50010
 Grant No. EC-00283-02
 Funds Awarded: $40,717
 Project Period: June 1, 1968 to May 31, 1971
OBJECTIVES:  To   perfect   a   recirculating
water-waste-handling system  using  existing
facilities and consisting of  an anaerobic la-
goon and  an  oxidation ditch. A laboratory
waste treatment pilot plant is  being operated
in such  a  way  as to simulate  a recirculating
waste treatment plant so that operational and
design criteria  can  be  determined. Manage-
ment implications such as cleanliness of  pens,
growth rate of swine,  and social  order are
being studied as well as optimum method ot
operation  so as to  avoid  adverse  effects on
the animals' and the operators' health.

APPROACH:  Samples  of  the   influent   and
effluent from the waste  treatment systems (an
anaerobic  lagoon  and  an  aerobic  oxidation
ditch) and the recirculating  water are  ana-
lyzed for their chemical, physical, and biologi-
cal properties,   namely, COD, BOD, solids,
coliform,  enterovirus,   pH,   and  chlorides.
All the  animals are examined routinely for
symptoms   of  disease  related   to  the waste-
handling system. Specific animal tests, which
have  previously been designed,  are used to
determine  the  influence of the handling sys-
tem on  the health  and growth  rate of the
animals.  Odor,  temperature,  and  humidity
are measured in the  confinement area,  and
the  laboratory-scale  waste  treatment  pilot
plant is operated so as  to permit evaluation
of the  overall  effectiveness  of the  proposed
recycle-water carriage-manure  system.

FINDINGS:   A recirculating hydraulic manure
transport system is in operation. Manure is
removed from   the  700-head  swine confine-
ment building  by hourly flushing 100 gal of
water into  the  two shallow gutters traversing
the animal  pens. The water flows down 42-in.
wide by 2-in. deep gutters, carrying  with it
manure accumulated since the previous flush-
ing. The animals have responded to this  sys-
tem by  depositing  all  feces and urine in  the
gutter,  and this keeps the remainder of  the
pens dry and free of manure.  When flushing
occurs,  the  pigs move  to the gutter  for diver-
sion and provide  the necessary  agitation to
suspend  the manure  solids in  the flushing
water. The result is a confinement building
in  which  no  manual  manure  removal is
necessary and in which there  is a  decidedly
lower  odor level than in comparable  build-
ings with other means ot manure collection.
 30

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No pen washing or other cleaning efforts are
used.
   From the building the manure  and water
flow by gravity into an anaerobic lagoon that
effectively removes the solids and reduces the
organic content of the liquid wastes. Effluent
from the  lagoon  is pumped  to  an oxidation
ditch for  further  removal of organic matter
and control of  odor. After settling to remove
solids,  the oxidation ditch effluent  is pumped
back to the flush  tanks in  the confinement
building for reuse.  The waste  treatment sys-
tem produces an effluent of acceptable quality
for reuse within the building, has not resulted
in disease problems within the  building, and
has eliminated  the need to haul  manure or to
discharge  effluent  into the  receiving stream.
   Construction currently underway will  al-
low wastewater from the building to  be di-
verted  directly  to  the oxidation  ditch. In this
mode  of operation, the  lagoon  will be  used
as a disposal method for excess solids from
the oxidation ditch.  Other aspects  of the sys-
tem will be unchanged.
   Soil  used as  a means of disposal for excess
lagoon effluent is applied at  rates up to 3 in.
per application at intervals of 3 to 5 days. This
high loading rate is managed  to promote maxi-
mum nitrogen  removal and results in essen-
tially  complete removal  of   organic  matter,
phosphorus, and bacteria while removing  60
to 70 percent of the nitrogen. Detailed studies
of nitrogen  transformations   and changes  in
the soil's organic matter  are  underway.

                 PUBLICATIONS

MINER, J. R. A review  of the literature  of 1967 on waste-
water  and water  pollution control. Industrial wastes.
Agricultural  (livestock)  wastes. Journal of the Water
Pollution Control Federation, 40(6): 1150-1158, June  1968.

HAZEN, T. E. Wiles of wet wastes. ASAE Paper No. 68-
556.  Presented at Winter Meeting, American Society of
Agricultural Engineers, Chicago, Dec. 10-13, 1968. 10 p.

KOELI.IKER, J. K., and J. R. MINER.  Use of soil to  treat
anaerobic lagoon effluent: Renovation as  a function of
depth and  application  rate. ASAE  Paper No.  69-460.
Presented at Annual Meeting, American Society of Agri-
cultural  Engineers, Lafayette, June 22-25, 1969. 19 p.

HAZEN, T. E., and J. R.  MINER. Waste-environment  com-
plex in confinement production of swine. In Proceedings;
Seventh  International Congress of Agricultural  Engineer-
ing,  Baden-Baden, Germany,  Oct.  6-9 1969. [St.  Joseph,
Michigan,  American  Society  of Agricultural Engineers.]
p. 197-203.

WILLRICH, T. L., and J.  R.  MINER. Anaerobic  lagooning
of swine wastes  In  Proceedings;  Seventh  International
Congress of Agricultural  Engineering, Baden-Baden, Ger-
many, Oct.  6-9,  1969. [St. Joseph, Michigan,  American
Society of Agricultural Engineers.] p.  287.

MINER, J. R. A  review of the literature o£ 1968  on waste-
water and  water  pollution  control. Industrial  wastes.
Agricultural (livestock) wastes. Journal of the Water Pol-
lution Control Federation, 41(6):1169-1178,  June  1969.

MINFR, J. R. The universities' role  in feedlot  pollution
control. In Proceedings;  Animal Waste Management  Con-
ference,  Kansas  City, Missouri, Feb.  1969.  U.S.  Fedeial
Water Pollution Control Administration, p. 23—25.

SMITH, R.  ].,  T. E. HAZEN,  and J. R. MINER.  Piggery
cleaning  using lenovated  wastes. Presented  at Symposium
on Farm Wastes, University  of New Castle Upon Tyne,
England, Jan.  7-8,  1970. 25 p.  (Iowa  Agriculture and
Home Economics Experiment Station Journal Paper  No.
J6435, Iowa State University.)      '

MINER, J. R., and T. L. WILLRICH. Livestock operations
and  field-spread manure as sources of pollutants.  Pre-
sented at Conference Concerning the Role of Agriculture
in Clean Water,  Iowa State University, Ames, Nov. 18—20,
1969.  (Iowa Agricultural and  Home Economics  Experi-
ment Station Journal Paper No. J-6378.)

MINER, J. R., E.  R. BAUMANN, T. L. WILLRICH, and T. E.
HAZEN. Pollution control—feedlot operations. Journal of
the  Water Pollution Control  Federation,  42(3):391-398,
Mar. 1970.
                 Effects of Processing  Poultry Manure on  Disease  Agents
                          Dr. James R. Howes
                   Poultry Science Department
                         Texas A&M University
               College Station,  Texas  77843
  Grant No.  EC 00316-02
  Funds Awarded: $63,596
  Project Period: June  1,  1968 to May 31, 1970
OBJECTIVES:   To investigate  the survival  of
disease agents in composted and dried  poul-
try wastes and the spread of the agents from
conventional  versus   composted   and  dried
                                                                                                  31

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waste products removed from poultry houses.
To determine the effects of variants in man-
agement during the  composting and  drying
of poultry wastes  of  different origin on the
chemical, physical, and pathogenic nature of
the end products.

APPROACH:   Manure produced by  domestic
chickens, turkeys,  and quail were studied to
determine the effects  of  species, sex, age,
management, nutrition, and environment  on
the physical, chemical, and pathogenic nature
of the raw manure. The various types of ma-
nure were then either composted or dried by
using some of the major variations of manage-
ment in processing that are likely to affect
the  end  product. The physical  properties
(particle size, density,  storage  stability, etc)
and chemical properties (pH, moisture, nitro-
gen, calcium,  phosphorus,  etc) of  the treated
manure were determined. During the process-
ing several parameters such as temperature,
humidity, and an air  pollution potential were
monitored. The use of various litter material
such  as  shavings,  sawdust,  rice hulls,  corn
cobs,  peanut hulls, and straw was studied to
determine their  effect on  the  composted
product.
  Litter scheduled for composting and ma-
nure scheduled for drying were seeded with
various pathogens associated with poultry to
determine the effect  of the management of
the two processes on the  survival of these
pathogens.  Specific  pathogens  studied  in-
cluded  the following:  Fowl pox  virus,  In-
fectious  Brusal Agent, Clostridia sp, Pasteur-
ella Multocida, Aspergillus flavus, Aspergillus
fumigatus Eimeria sp,  Ascaridia  sp, Raillie-
tina Cesticillus, Musca domestica, Bdellonys-
sus sylviarum, and Darlking beetle.

FINDINGS:
   1. The limitations of laboratory composting
of poultry wastes have been clearly demon-
strated. It is necessary to have  adequate vol-
ume  in  order to  simulate  field  conditions.
The  results  obtained from small units  are
highly suspect, at least 100  bird units being
necessary  to  provide  adequate  volume  of
wastes for working each treatment.
   2. Disease carryover in  composted poultry
wastes. Studies with Coccidia, Salmonella, and
Newcastle virus seeded in litter prior to com-
posting indicate  reduction in  active patho-
gens. Owing to overlong composting resulting
from inadequately sized  litter piles, the same
reductions  in  pathogen  numbers were ob-
tained with time. It is essential therefore to
have sufficiently  large piles  of manure dur-
ing composting in order to  obtain adequate
heating.
  Results from the past  2 years' studies indi-
cate that several species of bacteria and viruses
are not suitable  for a variety of reasons for
studying the  carryover  of disease agents in
poultry wastes. Coccidia and  nematodes ap-
pear to  be the  best  agents  with which to
work,  especially  since  these  agents  are not
highly contagious. Techniques developed to
control these agents would probably be effec-
tive for others since these organisms are rela-
tively  difficult to control.
  3. Ultraviolet irradiation of poultry manure
has been indicated to have distinct possibili-
ties  in controlling the  carryover  of  disease
organisms.
  4. Poutry litter materials  and composting.
It is possible  to  compost poultry  litter con-
sisting of any organic matter that has been
tried including corn  cobs, rice hulls,  peanut
hulls,  straw of various  kinds, sawdust, hard
and soft wood shavings, and so forth. The
environmental conditions prevailing  repre-
sent the main factor affecting speedy heating,
provided  adequate  air,  moisture, and  car-
bonaceous  and  nitrogenous  materials  are
present.
  5. Physical  properties of wastes  in relation
to  composting.  The  particle  size must  be
fairly  uniform and  small for the best com-
posting.  Too  fine  particle   size  causes an-
aerobic compaction, and overly large particle
size  permits  too  much  air to  penetrate the
pile.   Mineral content  of  poultry  manure
within the usual  limits has no apparent effect
on  composting,  and pH is  highly  variable
within and between piles that have supposedly
been subjected to similar treatments.
  6. Drying poultry wastes.  Provided a tem-
perature of some 200 F is reached for a few
minutes, pathogens evaluated  appear to be
destroyed.  Incinerators  therefore  provide a
disease-free material  but produce air pollu-
tion.  Dryers usually  well exceed  200  F and
 32

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should  therefore  also  provide   disease-free
processed  poultry wastes.  Mork  work is re-
quired  to  evaluate further the time-tempera-
ture factor with more pathogens.
  7. Reduction  in  the volume   of  poultry
wastes.  Traditionally  all  floor-raised  com-
mercial  poultry-broilers,  turkeys, most  re-
placement pullets, and many layer flocks are
raised on fresh floor litter. By composting the
litter between  broods it  has  been  demon-
strated  that the heat treatment controls most
active pathogens,  and the volume of litter
required  by the  poultry industry  has  there-
fore been greatly reduced. This is of economic
benefit  to the poultry industry, especially  as
competition increases for  sugar cane  wastes,
wood shavings, and other absorptive materials.
  From the standpoint of the volume of poul-
try solid wastes it is  estimated that 90 percent
of the broilers and many of the turkeys raised
during  the past 2 years  in the United States
have been raised  on recycled  litter, and the
volume of solid wastes for disposal has there-
by  been vastly reduced.  Furthermore,  the re-
sulting  stabilized  organic  wastes  do not  pol-
lute soil,  water, and air when distributed on
the  land as raw manure does.
  8. Manure from caged poultry.  Because  of
labor shortages and  economics many poultry-
men are  presently being forced to automate
their layer operations by  caging their birds.
Aerobic digestion of caged layer  poultry ma-
nure has been economically  established  and
is now  being used on a limited  scale  in the
United States to combat  fly  and  odor prob-
lems. Aerobic  digestion  will  control these
problems  and  has   enabled   some harassed
poultry operators to remain  in business.  In
addition the volume of the manure has been
greatly  reduced,  and furthermore stabilized
organic  material  eliminates soil,  water,  and
air pollution.
  9.  Cages for broilers.  Classically,  broilers
are raised on floor litter to avoid the develop-
ment of breast  blisters  and  leg  deformities.
Recent  studies under this grant  have  shown
that broilers  may now be raised  successfully
in  plastic-floored  cages  without  these prob-
lems. If the  cage system  is adopted  by the
poultry industry  for raising  broilers,  and  it
could  well  be the  case, the volume of solid
wastes produced by  broilers  in the  United
States  could be  further vastly reduced since
no  litter would have to be used.  The feces
could  also  be digested under  these  cages  to
reduce volume, control fly and odor problems,
and stabilize  the material in  order to avoid
odor, fly, and pollution problems when the ma-
terial is used  in  horticulture and agriculture.
  10. Composting of  cattle feedlot wastes. Al-
though outside the limits of the grant, assist-
ance  has been  given  to a  feedlot operator
in  Texas to compost feedlot  wastes. A pilot
operation has been highly  successful  in pro-
ducing a reduction  in volume and has resulted
in an odorless, stabilized agricultural fertilizer.
  11.  Composted  garbage for poultry litter.
Garbage from which  metal, glass, paper, rags,
and plastic  had been  removed was composted
by  Lone Star Organics, Jnc, of Houston. The
resultant material  has  been evaluated as an
absorbent   poultry  litter and found  to  be
highly desirable. Large-scale  field trials are
now in progress.


                 PUBLICATIONS

HOWES,  J.  R.  Methods of  disposal; poultry wastes. Texas
Agriculture Ptogtess, 14-22-23.  1968.
HOWES,  J. R. Management and  utilization of poultry
wastes.  Feedstufjs, 40(50):22-23, 1968.
HOWES,  J.  R.  The digestion of  poultry feces under cages.
Poultiy  Science,  47(5):682, Sept. 1968. (Abstract.)
HOWLS,  J. R.  How  to  manage poultry waste.  Canadian
Poultiy  Review,  93(3): 11-12, 38-39,  Mar. 1969.
HOWES,  J. R.  A  icview of available litter matciials  and
their advantages  and disadvantages. In Pioceedings, Third
National Poultiy Litter  and Waste Management Seminar,
1969. p. 140-149.
HOWES,  J. R. The  composting of  poultry  manure  and
litter and  its  use as a garden and feed fertilizer. Pre-
sented at  Pennsylvania  Ponltiy Waste  Conxeision Sym-
posium, Lancaster, 1969.
HOWES,  J. R., and J. W.  BRADLI v.  Composting gaibage
foi  poultry litter. Proceedings; Association of Southern
Agricultural Woikcis,  66:257, 1969.  (Abstiact.)
HOWFS,  J. R., and J. W.  BRADLEY. Littei  materials  and
management for  broilers. Poulti\ Science, 48(5):1822, Sept.
1969. (Abstract)
HOWLS,  J.  R., IV C. Woimeli, and B. R. STEWART. Cages
as enviionment  for  broilers. Poultiy  Science, 48(5):1822,
Sept 1969. (Abstiact.)
                                                                                             33

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               Research  on an Animal  Waste Pollution Control System
                      Dr. John  R. Thygeson
        Department of Chemical  Engineering
                          Drexel University
         Philadelphia, Pennsylvania  19104
 Grant No. EC-00390-01
 Funds Awarded: $52,048
 Project Period: Aug. 1, 1969 to July 31,  1972
OBJECTIVES:  To  investigate  the possibility
of rendering  animal  wastes  innocuous by
steam drying and to determine the nutritional
value of the dried wastes in hopes that they
can be  used as  animal feed.
APPROACH:   Three areas of investigation are
associated with this research effort, as follows:
the drying of the  animal  waste, characteriza-
tion of the  odors in  the dried waste, and
toxicologic  and nutritional studies of  the
dried waste. The drying  studies are  being
conducted on 1- to  5-lb samples of manure.
Factors  being determined  include  the  effect
of moisture content  of manure on drier op-
eration, the  effect of mass velocity on  both
heat transfer and mass transfer, the influence
of superheat in the  drying medium (steam),
the mechanism of  drying, the influence of bed
depth, effects of particle size and shape, and
the influence of nozzle orientation. Both or-
ganoleptic testing or  subjective evaluations
and analytical  testing by  means of gas-liquid
chromatography,   infrared spectroscopy,  and
mass spectroscopy  quantitatively and qualita-
tively define the  odors present in the dried
manure and the liquid waste  resulting from
the drying operation.
   Toxicologic  studies involve many chemical
tests, including pH and  alkalinity, and the
contents  of  iron,  phosphate, nitrate,  sulfur,
chloride,  water- and ether-soluble materials,
and nitrogen.  Animal  feedings  are used to
determine the toxic effects of the  dried ma-
nure. Those products found nontoxic are eval-
uated for nutritive value by being fed to rats.


FINDINGS:
   1. Equipment. An apparatus for conducting
through-circulation  drying tests with  super-
heated steam or with mixtures of superheated
steam  and  an inert gas  has been  designed,
built, and put into operation. The equipment
is suitable for the following limits on the dry-
ing parameters:
    bed depth up to 9 in.
    superficial fluid velocity up to  1,000 ft/
       min
    gas temperature to 350 F
    degrees of superheat to 140 F
    any mixture of superheated  steam with
       an inert gas
  Provision  for measuring drop,  flow, and
temperature,  is incorporated  in  the  system.
A Sanborn two-channel recording system pro-
vides  for continuous record of gas and pellet
temperatures  at several locations  throughout
the bed.  A  two-stage  electrical  heater and
superheater supplies  the energy  for  drying.
The exhaust vapor is continuously condensed
in a two-stage cooler-condenser system. Build-
ing supply steam, suitably reduced in pressure,
is the drying medium.
  2.  Experimental results. Preforming and
drying tests  on cow  manure obtained from
the University of  Delaware Agricultural Sta-
tion are in progress. Results thus far indicate
that a suitable preformed particle for through
drying can  be produced.  Pressure drop and
viscosity studies ae likewise  in progress.
  3. Theoretical results. A general computer
simulation of  the through-circulation  drying
process has been developed. The mathematical
model considers the case in which a constant-
rate drying wave  advances through  the bed
in the direction of steam flow and is  followed
by an expanding falling-rate drying zone. The
system of coupled  nonlinear  partial  differ-
ential equations describing temperature and
moisture content distribution  in fluid and
solid phases is solved by means of an explicit
finite-difference technique.
   The results  of the simulation study are
being applied to the optimization of the dry-
ing operation.
 34

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                  Survival'of Pathogens in Animal Manure Disposal
                       Dr. Stanley L. Diesch
       Dept.  of Veterinary Microbiology and
                              Public Health
                    University of  Minnesota
             Minneapolis, Minnesota  55455

OBJECTIVE:   To determine the survival and
subsequent public  health hazards of patho-
genic bacteria in cattle manure when disposal
is by means of extended aeration.  Laboratory
models  are used to determine the effect of
specific  field  environmental  conditions and
chlorination  upon the survival of Leptospira
pomona and Salmonella  typhimurium. Con-
currently, the detection  methods for these
pathogens are being compared and evaluated.

APPROACH:   Two laboratory-scale  models of
the extended aeration ditch were designed and
constructed.  One model is used for pathogen
survival studies and the other for establishing
engineering  design  criteria  before  its effect
on  pathogen survival is evaluated. Field en-
vironmental  conditions, including humidity,
dissolved oxygen,  pH,  and temperature, are
duplicated in the laboratory model for patho-
gen survival  studies. Known amounts of L.
pomona and S. typhimurium are added to
the  mixed  fecal  liquor  in  the  laboratory-
model system, and samples of mixed liquor,
sludge,  and effluent are collected during peri-
ods of seeding and postseeding to determine
the length of survival.  Survival of pathogens
is  also  studied  in chlorinated effluent and
holders immersed in the mixed liquor.

FINDINGS:  The department is using a 1:10
laboratory-scale model of an operational field
ditch.  In the field ditch the  department of
agricultural engineering is studying the treat-
ment of manure from beef cattle,  housed un-
der  confined conditions. The field  ditch is
used  for storage  and treatment and receives
manure from 36 beef cattle. After 6 months,
animals are removed, ditch  residues pumped,
and new tests begun.  Observed biological,
chemical, and physical data indicate a system
with  a  capacity of 50 cu ft per animal  can
store  and treat such wastes through the Min-
nesota winter period.
 Grant No. EC 00302-02
 Funds Awarded: $73,342
 Project Period: June 1,  1968 to May 31,  1971
  The operational laboratory model has been
developed and is being used to simulate  field
environmental  conditions  in  order to study
survival and detection  of  seeded  pathogenic
bacteria in beef cattle manure obtained from
the field oxidation  ditch. Improved methods
of measuring survival  and detecting epto-
spires in the manure have been developed by
the use of fluorescent antibody and artificial
cultural  isolation techniques. Repeated  sur-
vival  studies  have been  conducted  in  the
manure environment of Selas porcelain can-
dles, which allow a nutritional exchange  with
the liquid  media  of  the  laboratory ditch.
Studies have been conducted under simulated
field  conditions  with  varied pH,  dissolved
oxygen,  temperature,  and  total  solids.  Re-
covery of leptospires has been culturally made
up to  several  days  following seeding.  Lepto-
spires  have  been detected  by the  fluorescent
antibody  techniques  for longer  periods of
time.  Studies are being conducted in manure
effluents and  sludge-scale models  of settling
chambers under  varying environmental  con-
ditions. Leptospiral survival has been meas-
ured for several days and detection for longer
periods.  These findings  indicate that  a  defi-
nite  potential  health hazard  exists for  man
and animals.
   The department of agricultural engineer-
ing is using another laboratory-scale model of
the oxidation ditch. Studies are being made
to define solid  settlement  patterns and the
feasibility of the ditch as a means of separat-
ing undigested  feedstuffs having  nutritional
value  for reuse.  The  laboratory  model  has
been  used as an  effective tool on  changes in
rotor  design to control excessive foaming and
effect oxidation capacity.

               PUBLICATIONS

SOLAC, R. B. Survival of pathogens in animal manure dis-
posal.  Veterinary Medicine  Reporter, No. 24:lf{.,  Dec.
1969.
                                                                                       35

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                 Bacterial Contamination from Hospital  Solid  Wastes
                      Prof. Richard G. Bond
                     School of Public Health
                    University of  Minnesota
             Minneapolis, Minnesota  55455
 Grant No. EF 00007-04
 Funds Awarded: $147,473
 Project Period: Sept. 1, 1959 to  Dec. 31, 1963
OBJECTIVES: To study the microbial hazards
involved in solid waste handling and associ-
ated  housekeeping  procedures  in  hospital
areas.  To develop  and  demonstrate  solid
waste-handling methods designed to minimize
airborne  and  contact  contaminations  in  a
hospital environment.

APPROACH:   The investigation was conducted
in a 753-bed  teaching and research  hospital
and  a 265-bed private  general hospital. De-
tailed surveys, made of 5 solid waste categories
at 15 service areas, provided information on
the types  of materials in  each  waste  category
and  on generation,  routes,  and methods of
transport  from source  to ultimate  disposal.
Waste-handling activities  were simulated un-
der laboratory conditions where background
contamination could be controlled to measure
bacterial  dissemination.  Tracer  organisms
were also used to determine actual distances
under which microorganisms could be trans-
ported  through the hospital  after dispersal
into the environment.
  Air was extensively sampled  in the 15 serv-
ices and in waste-handling areas such as trash
and laundry chute terminal  points, trash and
laundry storage areas, laundries, and incinera-
tor rooms. Efforts were made  to devise and
demonstrate  remedial  measures  to  reduce
bacterial contamination emanating from hos-
pital solid wastes.

FINDINGS:   Perhaps the most revealing find-
ing  was  the  great complexity of  the  total
waste-handling operation. The  facts that han-
dling methods vary even  within a particular
service  and that usually no  single person in
the hospital can detail all the waste-handling
procedures attest to this  complexity. Never-
theless, the  survey  identified  the types of
materials  being discarded and  helped to pin-
point  some  of the  likeliest contamination-
generating activities for evaluation of micro-
bial  dissemination. It also yielded a  detailed
record of exactly how the various solid waste
materials are actually handled in a hospital,
pinpointed  some basically  unsound proce-
dures,  and suggested improvements.
  The need for a highly standardized method
of air  sampling of microorganisms was dem-
onstrated for any attempt  to compare areas
or situations. Ventilation patterns, movement
and  direction of air, and details of tempera-
ture and humidity were   all  shown to  be
necessary adjuncts to  a sampling program.
Care in selecting the sampling location—pref-
erably locations—within an area, based  on
knowledge of air movement, was indispensa-
ble.  The sequential sampling technique   (a
series  of samples  taken over  an extended
period),  together with   a detailed record  of
activities in the area, was shown to be  neces-
sary for describing meaningfully  the airborne
microbial  pattern of   any  area. With  this
method,  it was possible to obtain quantita-
tive  data comparing many  areas of  the  two
hospitals  and to demonstrate fluctuations  in
these levels related to specific activities, ven-
tilation differences, and housekeeping proce-
dures. It was shown that airborne contamina-
tion levels could be kept low  (less  than IO/
cu  ft) by strict  attention  to personnel and
traffic control, together with properly designed
ventilation systems and adequate housekeep-
ing  practices. Sharp increases  in air counts
were also detected, particularly those related
to  soiled-laundry-handling  procedures.   By
means of microbial "tracers" the paths of dis-
semination of contamination related  to waste
handling and to  other activities were tracked
through  the hospital.
  It proved extremely important to standard-
ize  the method of surface sampling of micro-
organisms. The very high variability  on most
surfaces  called  for collection  of very large
 36

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sample  sizes and the' randomization  of  sam-
pling sites to describe  adequately the surface
contamination of any  area at a given  time.
The partial working out of a detailed method
as part of the project was a major step toward
adequately evaluating  environmental surface
contamination.
   Another achievement was the development
of a mass characterization  procedure applica-
ble to  microbes  isolated  from the  environ-
ment.  With  this procedure,  data  were  ob-
tained concerning types as well as numbers
of environmental organisms; this information
is of vital importance in determining the po-
tential  significance  of microbial contamina-
tion.  Application of this  procedure  demon-
strated,  for  instance,  that  areas  having  the
smallest numbers of organisms tended to have
larger  percentages of  gram-positive  cocci  as-
sociated  with  dissemination  from  people;
"dirtier" areas had larger percentages of dust-
associated bacilli and molds.
   Studies of remedial measures produced the
following with regard to:
   1.  Laundry handling practices.  Airborne
contamination resulting from the  emptying
of loose linen from chutes added an  average
of 150 colonies/cu ft to the air near the chute
opening, and increased counts fourfold  or
fivefold, even  on the fourth  floor  (near  the
chute door). It was  found  that this contribu-
tion of  contamination could  be reduced  by
almost  75  percent by confining  the  linen in
impervious bags  and by almost 50 percent by
adequate ventilation of the chute. It was also
found   that  dissemination  on  upper floors
could be prevented by ventilation  that main-
tained negative pressure  in the chute.
   2. Environmental contamination in animal
surgery. A special area was set up in which
cleaning  and  disinfection, personnel dress,
and traffic (but not ventilation) were rigidly
controlled and compared with a similar  area
where there  were no such controls but where
the same surgical team could perform identical
procedures  on dogs. The  air-sampling data
collected for  some 34  complete days  in each
area revealed that, despite the lack of venti-
lation control, the "sterile" area maintained
a  mean  count of less than 20 colonies/cu ft
of air  compared  with  more  than  70 in  the
other area. Autogenous  factors  in  the dogs
themselves prevented an  accurate  determina-
tion  of  infection rates related to  environ-
mental contamination. However, deaths from
infection among all dogs in the "sterile" area
approximated  24  percent compared with  a
50  percent rate among dogs  in  the uncon-
trolled area. This suggests that a relationship
to environmental contamination exists.
  None  of the evaluated cleaning methods or
products consistently reduced the  microbial
count by as much as  80 percent immediately
following the cleaning procedure.  The count
on  the floor  built  up  in proportion  to  the
amount  of new traffic and activity in the area,
regardless  of  method  or product  used, and
continued to  rise  until  the day's  activity
ended.  No  significant difference   could be
determined between various germicidal prod-
ucts and control solutions using a nongermici-
dal detergent or ordinary hot  tapwater. Wet-
vacuum  pickup reduced the microbial count
slightly more than a standard mop-and-bucket
system did.


                PUBLICATIONS

GREENE, V. W., R. G. BOND, and G. S. MICHAELSEN. Air
handling systems must be  planned  to reduce the spread
of infection. Modern Hospital, 95(2): 136, Aug. 1960.

GRFENE, V. W.,  D.  VESLEV, R.  G.  BOND,  and G.  S.
MICHAELSEN. The engineer and infection control. Hospitals
(JAHA), 34(17):69, Sept. 1960.
GREENE, V. W.  and L. G. HERMAN. Problems associated
with suiface sampling techniques  and apparatus in the
institutional  environment.  Journal of Milk  and  Food
Technology, 24(8):262, Aug.  1961.
VESLEY, D. and  M  BRASK. Environmental  implications
in the  control  of hospital-acquitcd infections.  Nursing
Outlook, 9(12):742, Dec.  1961.
GRFENE, V. W  and D. VFSLEY. Method for evaluating
effectiveness of  suigical  masks  Journal of Bacteriology,
S3(3):663, Mar. 1962.
GREENE, V. W , D. VESLEY and K. M. KEENAN. New method
foi  microbiological  sampling of  sin faces  Journal  of
Rnctejiology, 84(1): 188, July 1962.
GREENE, V. W., D. VESLEI , R. G.  BOND,  and G.  S.
MICIIAFLSEN.  Miciobiological  contamination of  hospital
aii. I.  Quantitative studies.  Applied Microbiology,  10(6):
561, Nov.  1962.
GRIFM-, V. W., D. VFSI.EY, R. G.  BOND,  and G.  S.
MICHAFLSIN.  Microbiological  contamination of  hospital
air. II.  Qualitative studies. Applied Miaobiology,  10(6):
567, Nov.  1962.
MICIIAHSEN, G. S. Waste handling. In Proceedings; Na-
tional  Confetcnce  on  Institutionally Acquired Infections,
                                                                                           37

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Minneapolis, Minnesota,  Sept.  4-6, 1963. Public Health
Service Publication  No.  1188.  Washington, D.C.,  U.S.
Government Printing Office, 1964. p. 65.

VESLEY, D.  Surface sampling techniques for  the institu-
tional environment—present status. In Proceedings; Na-
tional Conference on Institutionally Acquired Infections,
Minneapolis, Minnesota,  Sept.  4-6, 1963. Public Health
Service Publication  No.  1188.  Washington, D.C.,  U.S.
Government Printing Office, 1964. p. 101.

MICHAELSEN, G. S. and D. VESLEY. Industrial clean  room
versus hospital operating rooms. Air Engineering, 5(9):24,
Sept. 1963.

VESLEY, D. and G. S. MICHAELSEN. Application of a sam-
pling technique to the evaluation of bacteriological  effec-
tiveness  of  certain  hospital  housekeeping  proceduics.
Health Laboratory  Science, 1(2): 107, Apr. 1964.

BULLOCK, W. E., J. W. HALL, W. W. SPINK, L. J. DAMSKY,
V. W. GREENE, D. VESLEY, and H. BAUER. A staphylococcal
isolation service: epidemiologic and clinical studies over
one year. Annah of  Internal  Medicine, 60(5):777,  May
1964.

MICHAELSEN, G. S. and  D. VFSLEY. Dissemination of aii-
borne microorganisms in an institutional environment. In
Surface Contamination;  Proceedings;  Symposium,  Gatlin-
burg,  Tennessee, June  1964.  B.  R.  Fish, ed.  Oxford,
Pergamon Press, [1967]. p. 285

VESLEY, D., and G. S. MICHAELSEN.  A technique for meas-
urement of  microbial contamination on flat  surfaces, hi
Surface Contamination;  Proceedings;  Symposium,  Gatlin-
burg,  Tennessee,  June  1964.  B.  R.  Fish, cd.  Oxford,
Pergamon Press, [1967]. p.  321.

BOND, R. G., and G. S. MICHAELSEN. Bacterial contamina-
tion from hospital solid wastes. Minneapolis, University
of Minnesota, Aug. 1964. 160 p.
                  Incineration of Infectious  and  Radioactive  Solid  Waste
                         Dr.  Leslie Silverman *
             Department of Industrial  Hygiene
                           Harvard  University
                Boston, Massachusetts  02115
  Grant No.  EF 00579-01 SI
  Funds Awarded  $52,122
  Project Period: Feb. 1, 1964 to  June 30, 1965
OBJECTIVES:   To investigate and analyze  the
performance characteristics  of a new  institu-
tional  incinerator-boiler facility designed to
dispose  of combustible,  infectious, and low-
level-radioactive biological solid wastes from
research laboratories and hospitals.

APPROACH:   Harvard  University's  incinera-
tor-boiler was  used to  investigate  its  use  for
disposal of  solid  waste  from  research  opera-
tions   and   hospitals.   Low-level-radioactive
solid  waste  incineration and  decontamina-
tion  were also  studied.

FINDINGS:   The performances of a crematory-
type  incinerator  and a  combination   steam-
boiler incinerator were compared in the com-
bustion of  difficult  laboratory and hospital
wastes  such  as animals  and  cage litter.  Be-
cause of excessive stack  emissions of  smoke,
fly ash, and malodorous gases  and vapors,  the
crematory type proved unsatisfactory.  Under
  * Deceased.
the  most  favorable  operating conditions for
avoidance of air pollution and for production
of a good-quality residue,  burning  capacity
was  only 2  to  3 Ib sq ft/hr. Higher  burning
rates produced severe nuisances.  The mecha-
nized steam-boiler incinerator, on the  other
hand, provided a sanitary method of handling
and   burning   these  wastes  efficiently  and
rapidly. A cyclone dust collector proved super-
fluous for use  with  gas  or oil fuels;  it could
be eliminated  without decreasing the overall
collection efficiency  of  an  electrostatic  pre-
cipitator that served as a final cleaning stage.
Viable bacteria  originating from  the charge
placed on the  hearth  of a  crematory-type in-
cinerator  were  recovered  in  the  flue  gases
whereas the  flue  gases from the combination
steam-boiler incinerator were always sterile.

                 PUBLICATIONS

FIRST, M. W., P. FILI.ES, and J. WALKI.EY. Disposal of low
level  radioactive  waste in commercial  incinerators.  In
Proceedings of the Ninth AEG Air Cleaning Conference,
Jan.  1967. p. 570-585.
38

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                  Hospital Solid Waste Disposal in Community Facilities
                   Professor Richard  G.  Bond
                      School of Public Health
                     University of Minnesota
             Minneapolis, Minnesota  55455
 Grant  No.  EC-00261-04
 Funds  Awarded:  $110,630
 Project Period: June 1,  1966 to May 31, 1970
OBJECTIVE:   To define the solid waste prob-
lems of hospitals as they relate to design and
operation of hospitals, to determine the im-
pact of hospitals' solid waste on community
facilities and operation, and  to  identify en-
vironmental health and safety problems asso-
ciated  with  present practices in hospitals and
their host communities.

APPROACH:   During  the  first year of  this
investigation five hospitals were  surveyed to
determine the  waste disposal  practices quali-
tatively and quantitatively.  Two were in a
large  city having  a  relatively  sophisticated
method of waste collection and disposal. These
two were of different  types and  sizes  to  pro-
vide different  Avaste characteristics. Another
two hospitals  were selected from suburban
communities where waste  collection and dis-
posal  programs  were  less  developed.  These
two also were  of different design and  opera-
tion. The fifth hospital was in a rural area
where  there were further differences in design
and operation  and in  the  community's solid
waste management.
  After survey techniques and investigative
procedures  had  been  developed during the
first year, 25 hospitals of different  sizes and
types   in  various  communities  around  the
country were studied during the  second year.
During the third year, the survey expanded
to about 100 hospitals. Again, these hospitals
were in different size communities and in dif-
ferent  geographical locations, were of various
sizes,  and  provided  various  services.  The
fourth year was devoted to the evaluation of
data,  development of recommendations,  and
publication of survey findings.

FINDINGS: Data are being  analyzed, and dis-
cussion of specific findings would be  prema-
ture.  Findings are expected, however, to in-
clude the following:
  An  analysis of  quantities of  solid  wastes
from  hospitals, indicating relation to number
of beds, patient census, numbers of staff and
students,  number  of  outpatients,  hospital
facilities,   community  setting,  and   other
factors.
  Classifications of quantities of solid wastes
from  hospitals according  to source  within
the hospital, type of solid waste,  and method
of disposal.
  Listings of the problems arising at hospitals
from  on-site  solid waste storage, treatment,
and disposal,  including compaction,  incinera-
tion,  grinding, bulk receptacles, and other
items.
  Descriptions of  conditions found at com-
munity  facilities  receiving  hospitals'  solid
wastes. The implications these conditions have
for hospitals'  solid waste disposal.


               PUBLICATIONS

BOND, R. G., and A. F. IOLAR. Hospital solid waste dis-
posal  in  community  facilities. Presented  at Engineering
Foundation  Research Conference,  Solid Waste  Research
and Development, Milwaukee, July  24-28, 1967. Confer-
ence Preprint No. D_3.
MICHAELSEN, G. S., and A.  F. IOLAR.  Disposing of dis-
posables.  Presented at Annual Meeting, American Hospi-
tal Association, Chicago, Aug. 21-24, 1967. 8 p.
                                                                                          39

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                             Study of Institutional Solid Wastes
                     Prof. Jerry C. Burchinal
             Department of  Civil Engineering
                    West Virginia  University
          Morgantown,  West Virginia  26506
 Grant No. EC 00265-02
 Funds Awarded: $120,037
 Project Period: Apr. 1, 1968 to Mar.  31, 1971
OBJECTIVES:  To  characterize  solid  wastes
qualitatively  and  quantitatively  from  the
West Virginia Medical School, which consists
of a general hospital, a basic sciences building,
and an  animal quarters.  In addition  to  the
usual  parameters  used to  describe, classify,
and characterize  solid wastes, considerable
attention is being given to the possible con-
tamination of such  material  by viruses and
bacteria. Sampling procedures were developed
to permit classification  and identification of
the  solid wastes according  to  source and to
the  particular producing  unit. It is  believed
that such information will be useful  in estab-
lishing safe procedures for  the  handling of
wastes exposed to pathogenic organisms and
in providing a basis for  the design of han-
dling and disposal facilities.

APPROACH: The waste from the basic sciences
building is collected from each floor and each
significant  unit  and  put into labeled bags.
The hospital  waste is collected and identified
by  grant  personnel  placed at  the  deposit
points on each floor. Waste brought to the de-
posit points is  placed by  the  observer in a
properly tagged  or colored  bag and  dropped
in a chute to the incinerator room.  Carcasses
and  combustible material  in the animal quar-
ters  are  incinerated.  Carcasses   harboring
pathogenic organisms are  autoclaved prior to
incineration. It is felt that with the exception
of a few microbiologic and virologic deter-
minations,  a  physical  description   of solid
waste from the animal  quarters  is adequate.
  The waste from each unit is analyzed physi-
cally for weight, volume, and  bulk density
and  classified  into 14 different categories such
as paper, cotton, and bottles. The  waste is
chemically studied for carbon, protein,  phos-
phorus,  nitrogen, carbon-nitrogen ratio,  sul-
fur, and hydrogen as well as for pH, moisture,
liquid content, volatile  solids and ash, and
gross   and  net  calorific   values.  Biological
studies include total count,  total anaerobic
count, aerobic and anaerobic spore  formers,
coliform count, staphylococci, beta hemolytic
organisms,  enterococci,  viruses,  and  fungi.
Survival of microorganisms in solid waste is
also studied by sampling composite waste held
at room temperature for  different lengths of
time.

FINDINGS:  The  annual  production  of solid
wastes from the hospital  and basic sciences
building is approximately  1,000 tons. This is
being classified according to the  amount pro-
duced by departments, to the amount per bed
in the hospital, and  to other unit quantities.
  A cost analysis of waste handling gave a cost
of $77.30 per ton of waste  handled.
  A  virologic study indicated  that viruses
could live in solid waste materials for approxi-
mately 3 to 5 days.
                PUBLICATIONS

ZEPEDA, F. Statistical analysis of institutional solid wastes.
Problem report submitted to  the Graduate School, West
Virginia University, in partial fulfillment of the require-
ments for  the degree of  Master of Science in Civil Engi-
neering. Morgantown, 1969. 59 p.

ARMSTRONG, D.  Refuse chute  sanitation.  Problem report
submitted  to the Graduate School, West Virginia Univer-
sity, in  partial fulfillment  of the requirements for the
degree of Master of Science in Civil Engineering. Morgan-
town, 1969.
40

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                              A Study of Incinerator  Residue
                      Dr. P.  Walton Purdom
  Department of  Environmental Engineering
                                and Science
                           Drexel University
          Philadelphia, Pennsylvania   19104
 Grant No.  Ul 00509-03
 Funds Awarded: $226,000
 Project Period: Jan.  1, 1965 to  Dec. 31, 1968
OBJECTIVES:  To  study incinerator  residue
of rotary kiln units and rocker-grate units, and
incinerator residue from municipalities not
having separate collection. To make a labora-
tory study by subjecting residue to tidal surg-
ing so that leaching and time release mecha-
nisms could be studied.

APPROACH:  Residue  samples were screened
to a  2-in.  diameter and magnetically  sepa-
rated, and  the  nonmagnetic  portion  was
shredded and  milled.  They were then ana-
lyzed for fats or  oil-soluble  fractions, water-
soluble fractions, ignition  residue,  nitrogen,
phosphorus,  potassium,  and  occasionally,
heavy metals. Odor, dust, and other nuisances
were  observed as well as fly and rodent attrac-
tion and  breeding.
   The effects of altering operating parameters
such  as feed rate, overfire and underfire air,
and  rate  of grate travel on residue were  in-
vestigated.  Bed  temperature  must be  high
enough to decompose all organic  material so
that rat and fly breeding is not supported. An
attempt was made to correlate  stack gas tem-
perature, residue bed  temperature, and the
organic content of the  byproduct residue.
   The effect of tidal  surging through incin-
erated residue  placed  in  a  varying  water
table  was investigated to determine if residue
is  suitable  from a  public  health  standpoint
for waterfront reclamation.  The  rilled area
was chemically  analyzed for  information  on
the time release mechanism  of leachable con-
taminants. Lysimeter studies and  analysis of
water-soluble fractions  were used.

FINDINGS:   The character of  incinerator resi-
due is determined by the degree of burnout,
which may be estimated by the weight loss
on ignition. Residue  with  greater than  90
percent burnout does not react biochemically,
and the major leaching problem is from inor-
ganic compounds. Major inorganics include
chloride in concentrations of 2,000  mg/liter,
sodium in concentrations of  3,500  mg/liter,
and phosphate in concentrations greater than
10  mg/liter. In  addition, the total  dissolved
solids are  increased  to 8,000 to  10,000 mg/
liter.
  For a landfill receiving only residue of less
than 90 percent burnout, temperatures of de-
composition  were  140 F. This indicates  that
an  incompletely burned residue  will decom-
pose similarly to unburned refuse.
  Rates at which leaching occur are  deceptive
and vary with the component. For  example,
iron is  quickly oxidized, and the concentra-
tion of iron in landfill leachate decreases rap-
idly. Conversely, the chloride and sodium con-
centrations are slower to develop,  but they
persist longer.
  Effects of operation on character of residue
indicate  that most incinerators  are  not con-
structed  with  sufficient operating flexibility.
Greater variation  in  total excess  air and in
the  overfire/underfire  ratio  should  be  in-
cluded. By altering  retention time  and bed
temperature  the degree  of burnout can be
increased.

                PUBLICATIONS
PURDOM, P. W. Characteiistics  of incinerator residue. In
1'iocecdiiigs of the First Annual Meeting of the Institute
for Solid Wastes of the American Public  Works Associa-
tion, Chicago, Sept. 13-15, 1966. p. 38-43.
PURDOM, P. W., and R. J.  SCHOENBERGER. Incinerator resi-
due. Limitations on use? Picsented at Meeting, American
Public  Health Association, San Francisco,  Nov. 2,  1966.
9 p.
SCIIOKNBERCER, R. J., and P. W. PURDOM. Classification of
incinciator residue. In Proceedings;  1968 National In-
cinerator Conference, New York, May 5—8, 1968. American
Society of Mechanical Engineeis. p. 237.
SciioKMiERCER, R. J., N. M. TRiEFF, and P. W. PURDOM.
Special techniques for analyzing solid waste or incinerated
                                                                                          41

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residue. In Proceedings;  1968 National Incinerator Con-
ference, New York, May 5-8, 1968.  American Society of
Mechanical Engineers, p.  242.

SCHOENBF.RGER, R. J., and P. W. PURDOM. Residue charac-
terization. Journal of the Sanitary Engineering Division,
Proc. ASCE, 95 (SA3):387-397, June 1969.

SUFFET, I., A. A.  FUNGAROU, R. J.  SCHOENBERGER,  and
S. J. LEVY. Specific ion electrodes analysis of wastewaters
from  solid waste disposal. In  Proceedings; Third Mid-
Atlantic Industrial Waste Conference, College Park, Md.,
Nov.  12-14, 1969. University of Maryland, p. 279-303.

SCHOENBERGER, R.  ].,  P.  W. PURDOM, S. J. LEVY,  and
H. I. HOLLANDER.  Characterization and treatment of in-
cinerator process waters.  In Proceedings;  1970 National
Incinerator  Conference,  Cincinnati,  May  17-20,  1970.
New  York,  American Society of Mechanical  Engineers.
p. 204-215.
                   Smokeless Incineration of  Bulky  Municipal Refuse
                         Mr. Elmer R. Kaiser
        Department of Chemical Engineering
                        New York University
                   Bronx, New York   10453
 Grant  No. EC 00248-05
 Funds  Awarded: $163,984
 Project Period: Feb.  1,  1964 to Jan. 31, 1970
OBJECTIVES:   To develop engineering data
necessary for the design  of  incinerators  for
burning oversize solid waste. To determine an
optimum time  for  consumption along with
minimum  emission  of smoke,  fly  ash,  and
noncombustible  residue.

APPROACH:   An existing experimental bulky
waste incinerator was modified  and tested to
determine  optimum conditions for  combus-
tion of  oversize wastes. Factors determined
included the temperature of inlet air, refrac-
tories,  and exit gases; drafts and draft  losses;
exit gas composition; capacity of exit gases;
and airfknv  rates.  The weight  losses of the
charges, gas  composition, heat  releases,  and
drafts were then plotted for the entire burn-
ing cycle. The volumes and densities of the
initial  charge and final residue were  deter-
mined and weight and volume  reduction ra-
tios established.
  A number  of  bulky  waste  incinerators
around the country  were studied in less de-
tail and their characteristics  evaluated with
respect to performance.
  Recommendations were prepared for the
sizes of flue gas passages, volume and configu-
ration  of the primary and  secondary  cham-
bers, types and  thickness of  refractory,  and
optimum width  and height  of  the charging
door.
FINDINGS:  A simple incinerator furnace has
been evolved, without  moving grates or stok-
ing mechanism, and without the  need for
shredding the refuse. Bulky waste is deposited
by dump truck in front of the charging door
and charged by tractor.
  The  charges are  burned  on  a refractory
floor in  a firebrick  chamber.  Air is supplied
through ports in the  floor, side walls,  and
arch.  Logs, tires, demolition lumber, furni-
ture,  mattresses,  and  other  materials  burn
until consumed in minutes or hours, depend-
ing on  their  thickness. Additional  charges
can be  added  as space becomes available by
the burning down  of previous charges. Sim-
plicity permits use  of semi-skilled labor. Fif-
teen to  eighteen Ib  are burned hourly per sq
ft of hearth area.
  Combustion of gases and smoke  from the
primary furnace is completed in the secondary
chamber. Although the amount of  fly ash
(dust)  in gases is small because  of  conserva-
tive rates of burning, flue gas-cleaning equip-
ment    (scrubber,  electrostatic  precipitator)
can be  added to clean gases to  any degree
required.
  The final report  (in preparation) will pro-
vide basic  design information and  perform-
ance to  be  expected. At  least two  full-scale
bulky  refuse  incinerators  based in  part on
these  principles  have  been  built  (Stamford
42

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and Norwalk, Connecticut) since  preliminary
findings became available.
  The findings  are expected to result in more
installations across  the country,  at consider-
able saving over other types  of incinerators.
Landfill volume  for  residue  is less than  10
percent that for unburned refuse.
                PUBLICATIONS

KAISER, E. R. The incineration of bulky refuse. In Pro-
ceedings;  1966 National Incinerator Conference, American
Society  of Mechanical Engineers, New  York,  May 1-4,
1966. p. 39-48.

KAISER, E. R. A new incinerator control  meter  is needed.
In Proceedings;  1966  National  Incinerator Conference,
American  Society of  Mechanical  Engineers, New York,
May 1-4, 1966, p. 176-182.

KAISER,  E. R. The incineration  of bulky  refuse.  II. Jn
Proceedings;  1968 National Incinerator Conference, New
York, May 5-8,  1968. American  Society of Mechanical
Engineers, p.  129-135.
KAISER,  E. R. Successful incinerators  are not   cheap.
Power, 113(9):78-79, Sept. 1969.

KAISER,  E. R. The mounting problem  of solid  wastes.
Power, 113(10):62-63,  Oct. 1969.
                 Systems  Analysis  of Shipborne Municipal  Incineration
                             Dr. Melvin First
           Department of Industrial Hygiene
                          Harvard University
               Boston, Massachusetts  02115
 Grant No. Ul 00557-04
 Funds Awarded: $455,163
 Project Period: Mar. 1, 1965 to June 30, 1969
OBJECTIVES:   To  investigate   the  scientific
and technical aspects of  ocean  burning of
municipal solid  wastes, including demolition
materials, and the disposal of residues at sea.
The effect of residue disposal upon the chemi-
cal water quality, as  well  as  upon living
things,  was  considered as well as  the effect of
such incineration on the air.

APPROACH:   Incinerator residues from land-
based operations were chemically  and biologi-
cally analyzed to establish their  composition
and their beneficial  and detrimental effects
on marine life. The deposition', distribution,
and floating characteristics of ash released on
surface water  over a 1- to 2-sq-mi dumping
area were investigated. An ecologic study was
made  to  establish the  effects  of continuous
shipborne incinerator operations  on marine
life. Moreover,  meteorologic studies  in  the
coastal  area  determined diffusion  of stack
discharges.
   Methods of stabilizing solid wastes for stor-
age up to 7 days were  studied  so that small
coastal  communities could  collect  and store
refuse  in a  sanitary  manner until sufficient
quantities have  accumulated to  warrant an
incinerator ship  stop.  Systems  analysis  was
used  to  establish optimum refuse collection,
location of dockage areas, quantity of refi'-e
to be  transferred per ship stop, and the op-
timum balance among  the incinerator  ship's
burning, traveling, and loading  times.

FINDINGS:   Typical   municipal   incinerator
residues contain 23 to 52 percent by weight of
particles less  than i/4> in.  in size. Larger  par-
ticles are mostly  metal cans and other large
metal  objects,  glass bottle  fragments,  and
stones. The biologically more active i/£-in. or
less fraction was used for bioassay studies,  and
the more  visible,  larger  fraction for studies
of residue stability on the ocean  floor. Heavy-
metal  concentrations in the  less than  \/2-'m.
fraction  of residue ranged from  10 ppm for
Cd and  60 ppm  for Cr  to 40,000  ppm for
Fe. Lead content was 700 to 10,000  ppm with
an average of 4,000 ppm  for six different in-
cinerator residues,  but the fraction soluble
in sea water  was less than 1 percent of  the
total and often below detectable  levels.
  Bioassays conducted with winter flounder,
quahaug,  mummichog,  shrimp,  menhaden,
lobster and  lobster larvae,  mullet, and  sea
                                                                                           43

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scallops failed to demonstrate acute  toxicity
associated  with  incinerator  residues  when
marine organisms were  exposed  to  residue
concentrations of 1 percent by weight or less
in sea water.  Twice weekly additions of resi-
dues  to harbor pens  containing quahaug for
37 months showed lower mortality and higher
growth rates  for residue-treated  clams and
more favorable responses from those treated
with  larger applications. The explanation is
believed to be related to a coarsening of the
silty  bottom  and the addition  of nutrients
from the residue. Similar long-term studies
on  winter flounder  showed  no  excess  mor-
tality after 7  months. No concentration of
heavy metals  was observed in any species.
  Direct observations of  residue behavior on
the ocean  bottom at depths  up  to  200 feet
over  periods  of  many months while  it  was
under the continuing influence of open ocean
currents and wave action generated by storms
indicated extreme stability of the deposited
material. Following a violent autumnal storm,
the maximum distance a half-gallon can was
observed  to have moved  was 50  ft  from its
original  deposition  site after  having  re-
mained motionless for the entire summer and
early fall. Repeated surveys indicated that fish
life  was markedly attracted  to  the  experi-
mental dump sites.
  Meteorologic studies have shown the great
steadiness of the  wind over the coastal waters
even  when wind speed  is moderately  high
and  have demonstrated  the probability that
for  any weather  pattern at least one  satisfac-
tory burning  site can be found  within a 10-
mile  run from shore that will  not  produce
air  pollution  on land.  Climatologic studies
indicate  that  the annual frequency  of days
unsuitable for sailing an incinerator  vessel
having the characteristics of a Liberty ship is
5, whereas  for a towed-barge operation the
number  of unsuitable  days  approaches 20.
Waste management during periods  of unfa-
vorable weather  can  be  by central storage at
dockside,  on-site storage by waste producers,
dockside  incineration using  gas-cleaning de-
vices and tall stacks, or land burial sites re-
served for these periods.
  The New York City Planning Commission
has been  studying ship incineration and has
come to the conclusion that costs will be only
slightly greater than for current disposal prac-
tices.  Engineering studies of burning equip-
ment and materials-handling equipment suit-
able for seagoing incinerator vessels indicate
that the limitless oceanic heat sink  may be
utilized as a  basis  for designing alloy  steel
water-wall burning chambers without heavy
and fragile refractory  linings that might be
damaged  by the constant motion of a ship.
The principles  of containerized handling of
ship's cargo appear to be suitable for  waste
handling  and easily adaptable to  incinerator
ship requirements.
  Manpower  requirements  will  be a major
cost item in the operation of a seaborne in-
cinerator, even with a towed incinerator ves-
sel. Recent developments in on-line computer
operation  of  chemical  and petrochemical
manufacturing plants and  electrical generat-
ing stations  suggest the application of this
concept to  the operation  of an  incinerator
with a minimum number  of men. It would
be possible to place incinerators on unmanned
towed vessels or  barges, and the associated
automatic control systems on the  tow vessel.
                PUBLICATIONS

SILVERMAN, L. Incineration of solid wastes at sea. APWA
[American Public Works Association} Reporter, 31:2, 4,
July 1964.

OVIATT, C. A. The effects of incinerator residue on selected
marine species. In  Proceedings of  the  Annual Eastern
Regional  Antipollution Conference, Kingston, July  22-24,
1968. University  of Rhode Island, p. 108-110.

FIRST, N.  W. Waste  incineration at sea and ocean disposal
of non-floating residues. Presented at 62nd Annual Meet-
ing, Air  Pollution Control Association, New York, June
8-12, 1969. Paper No. 69-33.
44

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                 Combustion Products from the Incineration of Plastics
                  Prof. Edward A. Boettner
             Department of Industrial Health
                     University of Michigan
               Ann Arbor, Michigan  48104
 Grant No. EC 00386-01
 Funds Awarded: $40,452
 Project Period: Aug. 1, 1969 to July 31, 1972
OBJECTIVES:  To  analyze  the  combustion
products of various  polymers,  and formula-
tions made from these polymers,  under a va-
riety of  conditions of temperature  and  air
supply.  Of primary interest are polystyrenes,
polyethylenes, polysulfones,  and  polycarbo-
nates. In addition, previous work, on  poly-
vinyl  chloride,  polyphenylene  oxide,  and
polyimide is being reported from the stand-
point of incineration  problems.  Some com-
bustion  runs are being done with secondary
burning so  that both complete  and incom-
plete incinerator conditions are approximated.

APPROACH:   A study  of  the mechanism of
thermal  decomposition of a plastic  is being
undertaken by using differential thermal anal-
ysis  (DTA)  and  thermogravimetric analysis
(TGA).   From  this information  it is being
determined  whether  the  plastic breaks down
in one continuous step or in a  series of steps
and also whether  the  reactions involved  are
exothermic or endothermic.
  A combustion furnace with controlled tem-
perature and air supply is being used to  gen-
erate decomposition  products for qualitative
and quantitative analysis.  The products  are
being collected and analyzed by  gas chroma-
tography, infrai'ed and  mass  spectrometry,
and other analytical methods.  Temperature,
airflow,  heating rates, and open flame are be-
ing investigated as  variables in the amount of
products  obtained   from   certain  plastic
formulations.

FINDINGS:  Research  on combustion products
of plastics since July  1969 has  included  con-
tinuation of work on two  plastics, polypheny-
lene oxide and polyimide, which was under-
way before the start  of this grant, as well as
preliminary studies on two new plastics, poly-
carbonate and polysulfone.
  On thermal  decomposition polyphenylene
oxide was  found  to  give  large amounts of
carbon   monoxide,   carbon  dioxide,   and
straight-chain and aromatic hydrocarbons as
volatile  products. In addition,  under  our
combustion conditions,  a  large  amount of
residue (~50 percent) as a viscous liquid con-
taining  high-boiling  phenols and  water was
formed.
  Polyimide undergoes the most nearly com-
plete  combustion of any  plastic  material
tested under the research project's combustion
conditions. Seventy percent of the plastic is
converted  to  carbon dioxide  and  carbon
monoxide on heating to 800 C. Water, am-
monia, oxides of nitrogen, cyanogen, hydro-
gen cyanide, benzonitrile, and benzene have
also been identified. Current work is on quan-
titatively accounting for the  nitrogen in this
plastic, which, because of the toxicity of the
cyanides  and nitrogen oxides, is extremely im-
portant.  No single analytical technique has
proved suitable for quantitation of these prod-
ucts, and a combination of gas  chromatog-
raphy and  wet  methods is being used.
  Work  on polycarbonate  includes  differen-
tial thermal analysis  and thermogravimetric
analyses  showing a  two-step  decomposition,
the first corresponding to a depolymerization
and the second to formation of carbon dioxide
and carbon monoxide  from  the  remaining
carbon  skeleton.  In  addition  to  these  two
major  products, methane,  benzene,  and to-
luene have been identified. Many more vola-
tile compounds  are  unidentified.  As  with
polyphenylene oxide, polycarbonate  forms a
viscous liquid residue accounting for about
50 percent of  the weight of plastic  burned.
In addition to  water, the major components
of this residue are phenol,  p-cresol, and p-
ethylphenol.
  We have also analyzed the combustion prod-
                                                                                      45

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ucts of  two plasticizers, diisodecyl  phthalate
and dioctyl  phthalate, commonly  used in
PVC. Pyrolysis of these plasticizers  results in
breakdown into a solid, liquid, and  gas phase.
The gas phase consists of COz, CO, hydro-
carbons through the butanes, and some  oxy-
genated compounds. The  liquid phase repre-
sents nearly pure plasticizer, which boils off,
plus some water.  The  solid phase,  composed
of long, white, needle-like crystals, has been
identified  as  phthalic anhydride, water,  and
the chain of the ester that is further decom-
posed into hydrocarbon fragments.
  A modified  combustion tube has been  de-
signed to allow insertion of two small flames
at the outlet  of the combustion furnace to
provide  secondary  burning and  to  parallel
more closely some  types of incinerator com-
bustion.  This modification is being evalu-
ated,  especially with respect to its  ability to
combust  the large  amounts  of liquid residue
from polyphenylene oxide and polycarbonate.
                  Continuous-Feed  Incineration  of Municipal Refuse
                       Mr. Elmer R.  Kaiser
       Department  of  Chemical  Engineering
                      New York University
                   Bronx, New York  10453
 Grant No. EC 00251-04
 Funds Awarded: $154,221
 Project Period: Sept. 1,  1965 to Aug. 31, 1970
OBJECTIVES:  To obtain  fundamental  engi-
neering data needed for better design of con-
tinuous-feed  solid  waste  incinerators.  Test
methods were  developed to determine the
variability of refuse composition; to determine
the  optimum  proportions  of  overfire  and
underfire air;  to determine heat release and
transfer in the burning refuse,  furnace, and
waste heat boiler; to evaluate the refractory
surfaces; and  to determine the  types  and
amounts of air and water pollution resulting
from the operation of the Oceanside Refuse
Disposal Plant in Hempstead,  Long Island.

APPROACH:  Full-scale tests were undertaken
on the Oceanside Refuse Disposal Plant. Test
methods were  generally  adopted from  those
used in the combustion of fuels and water
analysis, or were developed in  other  cases.
Samples of refuse taken  at  random intervals
were reduced in size and analyzed. The varia-
tion in moisture in the flue gas was monitored
and  related to the moisture total in the refuse.
The undergrate airflow was measured for each
of the  three windbox zones. The flow rate
through each of the  numerous overfire  air
nozzles  was determined,  and  the optimum
proportion of overfire air to underfire air was
determined  over a period of time  at given
loads by general performance, such as good
burnout of  the residue,  balanced furnace
temperatures, and freedom from smoke.  The
items for the heat  balance were  determined
by measurement and calculation, both input
and  output.  Residue output  was determined
on  a total  weight  basis, and samples were
analyzed for completeness of burning. Ther-
mocouples in the furnace walls and gas-sam-
pling probes were  used to gather pertinent
information. Gas samples were generally ana-
lyzed by Orsat apparatus, occasional samples
being analyzed by mass spectroscopy and other
techniques to determine the presence of minor
constituents.

FINDINGS:  Typical compositions and analyses
of  household  refuse  were  determined  for
winter  and  summer conditions. Paper  and
paper  products  comprise almost 50 percent
of the total, while  glass/ceramics and  metals
are each about 9 percent. The average refuse
is  28 percent moisture,  22 percent  noncom-
bustibles, and 50 percent combustibles, mainly
cellulose. Detailed  chemical analyses  were
run.  The   calorific value,  averaging 4,500
Btu, results from partial oxidation of metals.
46

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   The combustion process is'only partly com-
 pleted in the fuel level; hydrocarbons evolved
 from the refuse must be burned in the furnace
 space.  Overfire  air jets are essential  for this
 purpose. New design  data on nozzle sizing,
 air  pressure, and jet penetration  have  been
 reported in the  publications listed below.
   A simple system for calculating the heat
 and material  input and output of incinera-
 tion has been developed that is useful in cal-
 culating performance,  heat losses,  and so on.
   By  tests  on a  300 ton-per-day furnace the
 temperature  limits  and mechanism for  slag
 adhesion on refractory walls were established,
 as  well as  the  means for preventing  slag
 buildup. The refractory wall  must be cooled
 to  1,200 F  or lower to prevent  glass  from
 adhering.
   Incinerator  boiler tubes were eroded be-
 cause  fly ash acted as an abrasive when  mov-
 ing  more than 20 ft/sec through a boiler tube
 bank.  Corrosion  of boiler  tubes  was also ob-
 served as the result of deposits on the tubes
 as well as of flame impingement. The mech-
 anisms of fireside boiler  tube wastage will
 be summarized in the final  report. Waste heat
 boilers out of view of the  flames at other in-
 cinerators  have operated  for  years  without
 these problems.
   Recommendations  for  furnace  design  to
 achieve more nearly complete combustion are
 being  formulated as a  result of  the  project.
 Implementation  of  these  recommendations
 will  reduce  smoke emission,  carbon in  fly
 ash, and emissions of unburned gases, vapors,
 and particles  to  the atmosphere.

                PUBLICATIONS

 KAISER, E. R. A new  incinerator control meter is needed.
 In  Proceedings; 1966 National Incinerator Conference,
 New York, May 1—4, 1966. American Society of Mechanical
 Engineers, p. 176-182.
 KAISER, E. R. The sulfur balance of incinerators. Journal
 of the  Air  Pollution Control Association, 18(3):17I-174,
 Mar. 1968.
 KAISER, E. R., and  W. B. TRAUTWEIN. Prevention of fused
 deposits on  incinerator  lower side  walls. In  Proceedings;
 1968 National Incinerator Conference,  New York,  May
 5-8,  1968. American  Society  of Mechanical Engineers, p.
 136-141.
 KAISER, E. R., C. D. XEIT, and J. B. MCCAFFERY. Municipal
 incinerator  refuse  and  residue. In Proceedings;  1968
 National Incinerator  Conference, New  York, May  5-8,
 1968. American Society of Mechanical Engineers, p.  142-
 153.
 KAISER, E. R., and  J.  B. MCCAFFERY. Overfire air jets for
 incinerator smoke control. Presented at  Annual Meeting,
 Air Pollution Control Association, New York,  June  26,
 1969. Paper  69-225.
 KAISER, E. R. Incineration of packaging wastes with mini-
 mal air pollution. In  Proceedings; First  National Confer-
 ence on Packaging Wastes,  San Francisco,  Sept.  22-24,
 1969. Clemson, S.C.,  Clemson University,  p. 181-190.
                     Criteria for  Design and  Control  of  Incinerators
                         Or. Adel  F. Sarofim
        Department of Chemical Engineering
        Massachusetts  Institute of Technology
           Cambridge, Massachusetts   02139
 Grant No. EC 00330-01
 Funds Awarded: $68,672
 Project Period: June  1, 1969 to May 31, 1972
OBJECTIVES:   Primarily to  design a  labora-
tory-scale experimental  and  theoretical  pro-
gram  that will  yield data  pertinent to  the
control  of  conventional-design incinerators.
Models utilizing combustion on grates useful
for extrapolating existing  data to  new condi-
tions and  for optimizing  incinerator design
are being developed. Alternative schemes for
burning refuse are  also being evaluated.
APPROACH:  A number of design  and  oper-
ating variables are being investigated in an
attempt to find a variable that can  be related
to the  quality of  the residue  and  used  to
activate corrective action when the  unburned
fraction in the residue or in  the stack  gases
becomes  excessive. Included in  these varia-
bles  are excess air, fraction of air overtired,
longitudinal  distribution  of air above  and
                                                                                            47

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below  the  grate,  air  preheat,  refuse bed
height, and grate speed.
  An experimental study of combustion  is
being made on a stationary fuel bed simulat-
ing a section of a traveling-grate stoker. Com-
positions and temperatures in and above the
burning fuel bed, and infrared transmittance
across the top of  the bed  are being measured
in  detail.  Concurrently,  a  semiempirical
mathematical model  is  being designed  to
extrapolate  existing data  to new conditions
of operation or design so that operating con-
ditions  of the incinerator can be adjusted
to accommodate changes in the quality of the
refuse.

FINDINGS:   Efficient and clean incineration of
refuse requires dynamic control responsive to
the wide variations in  the size and composi-
tion of the refuse. The theoretical  and experi-
mental  programs in progress have  been de-
signed to provide a quantitative  measure of
the effect of random variations in the quality
of the refuse. The computational model  in-
cludes consideration of the drying, transient
heating,  pyrolysis,  and  residue  burnout  in
addition to the  complex  interaction of the
elements in  a bed.  The  overbed reactions
have been found to be controlled by mixing,
and this suggests that  considerable reduction
in overbed volume should be achievable  by
more  effective use  of  overfire jets. A labora-
tory-scale incinerator under construction,  in-
cluding continuous, detailed monitoring of
bed height, gas composition, and temperature
distribution, is being used to test the findings
of the computations and to explore different
methods of automatic  control of incinerators.

               PUBLICATIONS

SAROFIM, A. F. Combustion  reactions  in overfire volumes.
Presented to Grates and Combustion Committee, Incineia-
tor Division, Ameiican  Society of Mechanical Engineers.
[New Yoik], Jan. 15,  1970.  (Unpublished manuscript.)
                    Fireside Metal Wastage in Municipal  Incinerators
                           Dr. Paul D. Miller
        Department of Chemistry and Biology
                  Battelle Memorial Institute
                    Columbus, Ohio   43201
  Grant No. EC 00325-02
  Funds  Awarded:  $257,859
  Project Period: Mar.  1, 1969 to Feb. 29, 1972
OBJECTIVES:   To identify the conditions lead-
ing to fireside metal wastage in  solid waste
incinerators, to determine the mechanisms by
which metal loss occurs, and to devise correc-
tive measures  for  this situation. Both field
and laboratory studies are being conducted to
provide data on the environmental conditions
to  which metal surfaces are exposed  in  in-
cinerators and the effect of these conditions
on  metal wastage.

APPROACH:   Flue gas temperature, composi-
tion and velocity,  heat transfer rates, metal
temperatures, dust loading,  and composition
of deposits on metal surfaces are  being meas-
ured.  This information is  being related to
the characteristics of the refuse being burned,
the  rate  of  incineration, the conditions  of
combustion,  and the  design  of  incinerators.
  A special  probe comprising specimens  of
several  types of materials has been designed
and inserted into an operating municipal in-
cinerator. The probe was designed so that a
combination of water and  air  cooling  pro-
vides controlled temperatures.  A  thorough
physical and chemical examination  is being
made on the metals  and deposits  after their
removal from the incinerator.
  The laboratory studies help define corrosion
mechanisms and specific corrodents. Based on
these studies,  several  means of  alleviating
metal wastage  are  being investigated. These
include changes in  construction materials and
in furnace design, modification of combustion
48

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procedures, burning  of supplementary fuels,
and modification of solid waste fuel.

FINDINGS:  The presence  of  lead, zinc,  and
chloride in specimens of boiler tube  deposits
is the  most  significant  difference noted to
date between the deposits from  incinerators
and those commonly  encountered in coal- or
oil-fired boilers.
  Flue-gas samples taken  in  the New York
incinerator over a period of  24 hr showed
wide variations in the amount  of corrosive
gases present.  The  chloride  concentration
varied from 2.5 to 350 ppm, the fluoride from
0.27 to  3.3 ppm, and  the sulfur dioxide from
0 to 100 ppm.
  The  most  striking  difference  in the  flue
gas from an  operating municipal incinerator
in  Ohio as compared with a power  station
was  the presence  of significant quantities of
HC (up  to  115  ppm),  which probably re-
sults  from the  burning of certain types of
plastic materials.
  The  first corrosion  probe study was carried
out for a period of 507 hr, including 312 hi-
nt operating temperatures and  195 hr of shut-
down. Significant corrosion was noted on the
34  individual specimens. For  the most part
the  carbon  steels  exhibited  general  attack
while the stainless steels showed some inter-
granular corrosion. The  Type 304 stainless
steel was  the most corrosion resistant of the
alloys evaluated.
  Analyses of deposits built up on  the  cor-
rosion  probe during this 507-hr  exposure
period revealed a change in composition with
probe  temperature.  As the average tempera-
ture of the probe increased from 350 to 1,250
F and higher, the concentrations of aluminum,
silicon, magnesium, and  calcium in the de-
posits  increased. At the same  time the con-
centrations of iron, lead, zinc,  and potassium
decreased. The sulfate concentration along the
probe  was found to be fairly uniform regard-
less of  temperature while  the chloride con-
centration was less at the higher temperatures.
  Laboratory studies designed to provide con-
trolled  conditions  for investigating corrosion
of boiler tube materials by flue-gas mixtures
and boiler deposit  components have been con-
ducted. Synthetic flue gases consisting of typi-
cal mixtures encountered  in incinerators are
being  used with SO2 and  HC1 to  study  cor-
rosion of the same metals used in the probes.
The  metal  specimens  are in  contact  with
compounds  suspected  of being the  corrosive
agents.  Experiments  to  date  have  demon-
strated  that the corrosion  by  the  flue gases
alone is slight. When, however,  the metal is
in contact  with  a boiler  deposit component
such as lead chloride, corrosion is accelerated
(lead and chloride have been found in boiler
tube deposits). When the temperature is high
enough to  melt the  lead  chloride, the  cor-
rosion of the steels becomes severe.
                    Incineration of Plastics Found in Municipal Refuse
                  Dr. Richard W. Heimburg
       Department of Mechanical Engineering
                        Syracuse University
                Syracuse, New York  13210
 Grant No.  EC-00304-02
 Funds Awarded: $187,350
 Project Period: Mar. 1,  1969 to Feb. 29,  1972
OBJECTIVES:  To study systematically the de-
sti action  of  plastics  and  plastic-rich  refuse
by direct  burning and  by anaerobic heating
followed by burning  the volatile  matter. Of
particular interest are the chemical and  toxi-
(ological nature of stack effluent and the inter-
action of  the residue with water.
APPROACH:  Various  plastic materials com-
monly found  in domestic  solid waste, e.g.,
sheet  goods, foams,  castings,  or paper-sup-
ported films, are being evaluated for combus-
tion performance.  Each material is tested for
percentage  moisture,  volatile  matter, fixed
carbon and ash, and heat of combustion. The
                                                                                       49

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gaseous products of both  combustion  proc-
esses,  direct burning and anaerobic degrada-
tion followed  by combustion  of the volatile
components,  are being  analyzed  and  com-
pared. If warranted,  gas  liquid  chromatog-
raphy, spectrophotometry,  and other  more
definitive procedures are employed. Toxicity
studies are made by exposing  rats and plants
to the gaseous effluent of the two combustion
methods.  In  addition  to percent  reduction,
the interaction of the various residues with
water is  being determined for reduction of
BOD and for effect on water ecology.
FINDINGS:   The first  year  of  the grant was
devoted to building a flexible model incinera-
tor, developing the necessary  analytical  pro-
cedures, and setting up equipment and  pro-
cedures for the toxicity studies.
  The model incinerator can be either batch
fed or continuous; a wide variety of primary
chamber and afterburner conditions is availa-
ble. A movable probe in  the afterburner per-
mits GC  analysis "on-line" to trace  the de-
struction of the more  refractory compounds.
  The sample is'continuously drawn into the
stainless steel tip of the probe and cooled im-
mediately to  a  predetermined temperature
between the ice  point and 200 C. The high-
boiling fractions are  immediately condensed
in the tip of the probe.  (These are later ex-
tracted and analyzed separately.) The remain-
der of the inducted gas is now available  to
a total-hydrocarbon detector and a concen-
trator. After a given period of time  a con-
centrated  sample  can be fed  either  to the
total-hydrocarbon  detector,  a  thermocouple
detector, or a GC column. Our greatest dif-
ficulty has been  that  gas mixtures have been
too dilute for our apparatus. We have only
recently rectified  this with the adoption  of
a different concentration  technique.
  The gas that  does not enter the probe is
cooled to just  above the dew point  of  its
water. The  fly ash  is  then  collected and
analyzed by size and composition.
  Finally, the effluent is  introduced to vari-
ous plant and animal exposure chambers. By
dilutions  with clean,  dry air, it is possible to
subject these organisms to various humidity
conditions and temperatures.
               Fly and  Economic Evaluation of  Urban Garbage Systems
                         Mr. Dean H. Ecke
                   Vector Control Specialist
            Santa Clara County Health Oept.
               San Jose, California  95128
 Grant No. Ul 00690-01
 Funds Awarded: $45,879
 Project Period: May 1, 1966 to Apr. 30,  1967
OBJECTIVES:  To compare entomologic  and
economic evaluation of once-a-week garbage
can service; twice-a-week garbage can service;
once-a-week  pickup from suspended  paper
bag containers; and twice-a-week service with
paper bag containers.

APPROACH:   Four  economically comparable
residental areas of approximately 500  homes
each were  studied in the  city of Santa Clara,
California, an  area for each of the four  sys-
tems. Paper bag containers were installed in
two  areas and use  of  standard garbage cans
continued in the other two areas. Collection
service  was altered  so  that  both once- and
twice-a-week service could be  compared be-
tween areas for each system. The new pickup
schedules started about  1  month before the
collection of data began so that residents and
the collection company could become familiar
with the new systems. Maggot  traps were in-
stalled under 40 representative units in each
area from which all  migrating fly larvae were
collected. Adult fly  density  was detected by
using 20 standardized attraction stations  in
each of the four areas. The entomologic  evalu-
50

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ation  was  determined  from  the  combined
adult and larval fly counts as  they related to
fly densities and fly problems during 8 weeks
in August and September 1966.
   The  economic evaluation was primarily a
time and motion study that compared  the
various aspects of the  pickup service among
the areas.

FINDINGS:   The study indicated that the  fre-
quency of collection was probably more  im-
portant than  the type of system or container
used, and although there was  a reduction in
fly numbers from once-a-week paper over once-
a-week  cans,  the reduction was not enough
to  suggest adequate  fly control. Both of  the
twice-a-week  systems showed  substantial re-
duction  in fly  production, but the twice-a-
week can system would probably require con-
siderable  follow-up  to  achieve  satisfactory
control. Twice-a-week paper bags did achieve
satisfactory fly control.
   It was  also found  that as much as 30 per-
cent savings in manpower  could be achieved
by substituting paper  bags  for metal  cans
but that  unless the collection  system was ac-
tually engineered around the paper bag con-
cept the  saving in time would probably  not
be sufficient  to  pay for the additional cost
of the bags.
   In conclusion, the following findings were
made.
   1.  Once-a-week  can  containers  produced
excessive numbers of flies in about 67 percent
of the containers, while 10 percent of twice-
a-week cans  produced significant numbers of
green blow flies. The once-a-week paper con-
tainers produced  flies in 20 to 25 percent of
the  containers while  the  twice-a-week paper
containers had no containers with consistently
high fly production.
   2.  Frequency  of garbage  service  was an
important control factor, since neither of the
once-a-week systems achieved satisfactory con-
trol,  whereas  the twice-a-week systems  did
produce substantial control.
   3.  Individual garbage containers are inde-
pendent fly sources with little or no  depend-
ence on nearby sources for their productivity.
   4.  Twice-a-week  garbage  service  to   sus-
pended  paper bag containers could  achieve
control of green  blow flies provided that the
community  would  be  willing  to  bear  the
increased costs of the paper  sacks and  that
100  percent  of the residences were included
in the service.

               PUBLICATIONS

ECKE, D. H., and D. D. LINSDALE.  Fly and economic evalu-
ation of urban  refuse systems. I. Control of green blow
flies  (Phoenicia) by  improved  methods of residential
refuse storage, and collection. California Vector Views,
14(4):19_27, Apr. 1967.
ROGERS, P. A., and G. L. BELLENCER. Fly and economic
evaluation of urban  refuse systems. II.  An efficiency
analysis of paper bag containers.  California Vector Views,
14(5):30-37, May 1967.
                           Integrated  Control of  the Housefly
                      Dr. Richard C. Axtell
                  Department of Entomology
             North Carolina  State  University
             Raleigh, North Carolina   27607
 Grant  No.  EC 00246-06
 Funds  Awarded:  $77,203
 Project Period: Sept.  1, 1963 to June 30, 1970
OBJECTIVES:   To explore factors affecting the
attractiveness  of  houseflies  to various  preda-
ceous,  manure-inhabiting mites and to study
the susceptibility of these mites to insecticides
commonly used for houseflies.
APPROACH:   Two specific studies were  con-
ducted. In one study, mixed populations  of
manure mites  were examined  to determine
if the combination of different species results
in higher frequency of predation and phoresy.
                                                                                        51

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Further work was carried out to isolate the
pheromones present  in manure and in house-
flies responsible  for  the  attraction  of mites.
Microsurgery  techniques with a  laser  beam
were used to investigate in greater detail the
role of certain sensory  areas in the mite for
attraction.
   In the  other  study,   16  compounds  were
laboratory  tested to  determine  the compara-
tive  toxicities   of  various insecticides  for
housefly  larvae  and predaceous  mites.  Ad-
ditional insecticides  were screened  for  toxic-
ity,  and  promising  compounds  underwent
field evaluation.

FINDINGS:   An integrated fly control program,
based on selective application of insecticides
to the resting sites of the flies and encourage-
ment of  manure-inhabiting predaceous  mite
populations,  has been  developed for caged-
poultry houses.  This  program  reduces the
amount of insecticide usage and cost.
   The sensory structures of the housefly and
a predaceous macrochelid mite have been de-
termined  and  examined by electron  micros-
copy. It is possible now  to study the behavior
of these  insects  in  more detail and  develop
methods of increasing the predation rate and
altering the habitat  to reduce the survival of
fly larvae.

                 PUBLICATIONS

AXTELL,  R.  C.  Phoretic  relationship  of  some  common
manure-inhabiting Macrochelidae (Acarina: Mesostigmata)
to the house fly. Annals of the Entomological Society of
America, 57(5):584-587, Sept. 1964.

O'DONNELL, A. E., and R. C. AXTELL. Predation by Fus-
curopoda vegetans  (Acarina: Uropodidae) on the house
fly  (Musca  domestica).  Annals  of  the  Entomological
Society of America, 58 (3):403-404, May  1965.

FARISH,  D. J. Some aspects of  the sensory and phoretic
behavior of Macrocheles muscaedomesticae (Scopoli, 1772)
(Acarina: Macrochelidae) with a consideration of phoresy
as a phenomenon. M.S. Thesis, North  Carolina  State
University at Raleigh, 1965. 151 p.

FARISH,  D.  J.,  and R. C. AXTELL. Sensory  functions of
the palps and first tarsi of Macrocheles muscaedomesticae
(Acarina:  Macrochelidae),  a  predator of  the house fly.
Annals  of the Entomological Society of America, 59(1):
165-170, Jan. 1966.

AXTELL,  R.  C.  Comparative toxicities of insecticides to
house fly larvae  and Macrocheles muscaedomestica,  a
mite predator of the house fly.  Journal of Economic
Entomology, 59 (5): 1128-1130, Oct. 1966.

AXTELL, R. C. Integrated house fly control: Populations
of fly larvae and  predaceous mites, Macrocheles muscae-
domesticae, in  poultry manure after larvicide treatment.
Journal of Economic Entomology, 61(l):245-249, Feb. 1968.

WILLIS, R. R., and R. C. AXTELL. Mite predators of the
house fly: A comparison  of Fuscuropoda vegetans  and
Macrocheles  muscaedomesticae.  Journal  of Economic En-
tomology, 61 (6): 1669-1674, Dec. 1968.

AXTELL,  R. C. Macrochelidae (Acarina:  mesostigmata) as
biological agents for  synanthropic flies. In G. O.  Evans,
ed. Proceedings of the Second  International Congress of
Acarology, University of  Nottingham, Sutton Bonington,
England, July  19-25, 1967. Budapest, Akademiai  Kiado,
1969. p.  401-416.

PARISH, D. J.,  and R. C. AXTELL. Phoresy redefined and
examined in  Macrocheles  muscaedomesticae (Acarina:
Macrochelidae). Acarologia. (In press.)

AXTELL,  R. C. Integrated  fly-control  program for caged-
poultry houses. Journal of Economic Entomology, 63(2):
400-405, Apr. 1970.
                   Succession and  Ecology of Diptera in Cattle Droppings
                        Dr. John R. Anderson
                   Department of Entomology
                             and Parasitology
             University of California—Berkeley
                   Berkeley, California  94720
  Grant No.  EC 00252-05
  Funds Awarded: $77,326
  Project Period: Oct. 1, 1963  to Sept. 30, 1970
 OBJECTIVES:   To  study  cattle  droppings  as
 ecologic  units and to examine  the extent  to
 which the  inhabitant organisms contribute  to
 the  breakdown  and  recycling  of individual
 droppings.
APPROACH:  The  cowpat  habitat  is  being
studied, under  both undisturbed pasture and
experimental  conditions,  to  determine  the
succession  and  density  of  various  Diptera
species that inhabit the droppings.  The time,
 52

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place, and pasture habitat in which  individ-
ual cowpats are dropped are being  assessed
to determine how these factors affect surface
succession and  the subsequent fauna  that de-
velop in  and  emerge  from  such  pats. Both
naturally dropped and experimentally exposed
pats of  known sizes are being studied.
  The  interrelationships  between  fauna are
being assessed by standardized sampling meth-
ods  to  determine  the relationships  among
numbers and  species of arthropods, the rate
of cowpat degradation, the  recycling of nu-
trients,  and the effects of  natural enemies on
pests such as  horn and  face flies.  Because
the  face  fly, Musca  autumnalis,  is  not yet
present  in California, another aim is to study
the impact of an exotic species on  the native
fauna (or vice  versa).

FINDINGS:  The feces of  larger  animals, es-
pecially ruminant herbivores, are utilized as
food and shelter by a large number of animal
species,  especially arthropods. There  is a dif-
ference  between the habitat of undisturbed
cattle droppings as  they lie in pastures and—
as in a feederlot—that of  cattle  dung  dis-
turbed  by man and heaped into manure piles
or  trampled by cattle in close confinement
and mixed with urine. In California pastures,
109 different species of flies visited fresh cattle
droppings, and at least 50 are known to have
developed therein. By contrast, larvae of only
seven fly species have been found in droppings
in feederlots. The next largest order of arthro-
pods collected in pastures  was the  Coleop-
tera, of which  35 species  of  beetles occurred
in  droppings  in both the  adult  and  larval
stages. Most of the  fauna  of  undisturbed cat-
tle  droppings also inhabit the feces of native
wild herbivores such as bison and moose, but
the  pellet droppings of deer, elk, and  wild
and domesticated sheep  are unsuitable for
this  fauna.
  Publication of the first key to the  families
and  major genera of flies that breed in un-
disturbed cattle droppings, including  18 fami-
lies and 24 genera  and annotations for  most
of the  50 species,  filled  a  void.  Since  the
faunae  of undisturbed cowpats generally are
widely distributed wherever  there  are cattle,
the key  and the accompanying description and
discussion  of  these  faunae  serve  as  a basic
guide  to  the insects  associated with  fresh,
undisturbed  cattle droppings  in California
and elsewhere in the United States.
  In pasture  situations, cattle feces  are  not
likely to contribute to disposal or pollution
problems, because of the role the indigenous
arthropod faunae play in the biodynamics of
individual  droppings—the flies,  beetles,  and
other inhabitants  constitute important com-
ponents of the pasture ecosystem because of
the part they play in the breakdown and re-
cycling of individual droppings.  Most faunal
members of the pasture community are bene-
ficial  and  unobtrusive species;  few  persons
even know they exist.  The only pests associ-
ated with pasture feces are the obligate, host-
specific parasites of cattle and bison—the horn
fly, H. irritant, and the  face fly, M. autumnalis.
Only the face fly is an occasional pest  of other
animals  (and sometimes  of man when it is
hibernating in houses).
  Under range of pasture conditions, neither
the house  fly or the stable fly, 5.  calcitrans,
oviposits or develops in the individual live-
stock droppings.  On the other hand,  house
and stable fly larvae become the predominant
species in droppings when cattle are confined
in feederlots.  When large numbers of cattle
are confined in  feederlots, horn and face fly
populations are reduced to insignificant num-
bers because droppings are rarely left undis-
turbed, and  almost all other  "unobtrusive
pasture flies" are  excluded from  this  "un-
natural habitat."  In place  of  the  two host-
specific pest species  mentioned, the feederlot
frequently produces immense populations of
house and stable flies. These two very noxious
pests affect a  wide range of animals  and  can
and do affect  man directly. The stable fly ob-
tains  blood  from all  types  of domesticated
mammals and is often  a more serious pest of
cattle than the horn fly. The feederlot is, then,
a prime ecologic example of how catastrophic
fluctuations  in  densities of  certain  insects
(usually pest species) occur when man changes
complex ecosystems into simple ones,
  In pastures, the faunal composition on  and
within  each  fresh  pat  varies  considerably;
among other things, this depends upon when
and where the pat is dropped. Pats dropped
at night or on cold  days form  a crust before
the usual  early-stage  inhabitants are active
                                                                                       53

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and are, therefore, excluded. Pats dropped in
the shade may have distinctly different faunae
than  those in sunny locations,  especially in
hot  weather.  The  factors determining the
faunal  composition  of  individual fresh  pats
derive  from  the  fact  that  populations of
different  species are confined to various pre-
ferred  local  habitats or  activity  areas  in a
pasture.  Each area  has   constantly  shifting
boundaries,  and each  species   has  different
characteristic  environmental    requirements
and   powers  of  dispersal. In  addition, the
number of pats dropped  in a  specific locale
at or near the same  time  and diurnal fluctua-
tions in insect activity influence the numbers
and kinds of insects  that will eventually reach
and colonize a fresh pat.
   Each dropping  is a  discrete  habitat  unit,
and the numbers of larvae of coprophagous
and predaceous  species of insects interacting
with  each  other as they develop are deter-
mined  by the number of larvae hatching from
eggs  laid by females on each dropping in the
first few hours; after that, essentially no more
prey  or  predators  are   introduced.   Experi-
mental studies reveal that larvae of the copro-
philic  Diptera have a  remarkable ability  to
complete  their  growth  from   egg  to  pupa
under  a  wide variety of physical conditions.
Competition for food or space seems rarely,
if ever, to be a mortality  factor to larvae  of
the  coprophagous  species. In  general, after
the  female lays her eggs in a  dropping, the
hatched  larvae  in  an undisturbed dropping
are quite certain of completing their growth
to pupation unless killed by  a predator  or
parasite. Other studies reveal that under nat-
ural field conditions, the mortality of copro-
phagous  species  of  Diptera  reared   from
droppings is correlated with the numbers  of
predators in each dropping.
  The  elimination of the  normal faunae  of
individual  cattle  droppings in  pastures by
mechanical means or treatment  with  insec-
ticides  results  in a prolonged period's being
required for pat degradation and a consequent
loss of  usable  acreage for grazing.
                PUBLICATIONS

ANDERSON, J. R.  Biological  interrelationships  between
feces and flies. In  Management of Farm Animal Wastes;
Proceedings;  National Symposium on Animal Waste Man-
agement, East Lansing, Michigan, May 5-7, 1966, Kellogg
Center  for  Continuing Education, Michigan  State  Uni-
versity. ASAE Publication No. SP-0366. St. Joseph, Mich.,
American Society of Agricultural Engineers, p. 20-23.

ANDERSON, J. R. Recent developments in  the control of
some arthropods of public  health and veterinary impor-
tance. Muscois flies. Bulletin  Entomological  Society of
America, 12(3): 342, 1966.

FOSTER, W.  A. Co-operation by male  protection of ovi-
positing female in the Diptera. Nature  (London), 214
(5092):1035-1036, June 3, 1967.

POORBAUCH,  J. H., J. R.  ANDERSON, and  J.  F. BURGER.
The insect  inhabitants of  undisturbed cattle  droppings
in Northern California.  California Vector Views,  15(3):
1-36, Mar.  1968.

ANDERSON, J. R., and J. H. POORBAUGH. New livestock fly
moves  toward state.  California Agriculture, 22(3):406,
Mar. 1968.

FosrER, W.  A. Predatory  behavior of Scatophaga ster-
coraria (Diptera:  Anthomyiidae)  in California.  Annals
of the Entomological Society of America, 63(l):338-339,
Jan. 1970.
                Dynamic  Evaluation  Procedure; Refuse-Handling  System
                       Dr. Bobby C. Spradlin
               School of Industrial Engineering
               Georgia Institute of Technology
                     Atlanta, Georgia  30332
  Grant No.  Ul 00513-02
  Funds Awarded: $58,823
  Project Period: Sept. 1, 1966 to Feb. 28, 1969
 OBJECTIVES:   To detail a descriptive simula-
 tion  model  of a  solid waste management sys-
 tem  in  a cooperative study with the city of
 Atlanta,  Georgia. To evaluate  the effects of
 changes made in the system as a result of the
 study.
 54

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APPROACH:   The  perspective  used  in  this
study is called  industrial dynamics  (J. W.
ForresterJ), which grows  out of four  lines
of earlier development: information feedback
theory,  automatized military tactical decision
making, experimental design of complex sys-
tems by use of models, and digital computers
for low-cost computation.  This concept may
be used to  treat the  interactions  among the
flows of information, money, orders, materials,
personnel,  and capital  equipment in an in-
dustrial system.
  This  study used  the solid  wastes  system
of the city  of Atlanta to collect data.  Using
this information,  the research called  for de-
signing a model to portray systems behavior,
providing a procedure for evaluating various
proposals  as potential  system  improvements
from  a  standpoint of economy and efficiency,
  1 FORRESTER,  J. W.  Industrial dynamics,  Cambridge,
M.I.T, Press, 1961, 464 p.
providing insight into the  basic nature  of
the variables  inherent in  a solid waste sys-
tem, and possibly disclosing new important
variables.
FINDINGS:   Long-term control  of solid waste
pollution  must  be obtained  by controlling
the  generating  source of  the problem—at
manufacture.
  Short-term  waste  treatment  costs over  a
given period  of time  for  a  given level of
problem seem to vary  widely  depending on
the rate at  which resources are spent  to ac-
quire the treatment capacity.
  Considerable savings can probably be made
on short-term treatment costs by focusing on
the accumulations in the system. Application
of the research grant findings was determined
capable of reducing by 50 percent the annual
operating costs  of a major Florida city,  if
implemented.
                    Mathematical  Analysis of Solid Waste Collection
                        Dr. Jon  C.  Liebman
Department  of Geography and Environmental
                                Engineering
              The  Johns Hopkins University
                Baltimore, Maryland  21218
 Grant No. EC  00309-01
 Funds Awarded: $15,190
 Project Period: Mar. 1, 1969 to Feb. 28, 1970
OBJECTIVES:   To determine optimal location
of transfer stations and other facilities by use
of a mathematical model, to investigate the
effect of parameter changes  on  optimal poli-
cies, and to  determine optimal  routing of
collection vehicles.

APPROACH:   This  research  effort  is  an ex-
tension  of  the work done  under research
grant  UI-00539-02  "Optimal  Policies for
Solid Waste Collection." An analytical model
to determine  the optimal location, type, and
size  of  transfer  stations was developed to
minimize the  overall cost  of transportation
and  facilities. The values of the various em-
pirical costs and coefficients included in the
model  were  determined from  data already
gathered in the previously  mentioned  grant.
Included  were the cost of transportation as
a function of collection frequency, crew size,
vehicle type, household  density,  haul  dis-
tance,  and amortization policies.
  Sensitivity analysis to show how  the opti-
mal location and cost are affected by changes
of parameters was carried out for  variables
such as household density, frequency of col-
lection, haul distance,  crew size, type  of ve-
hicle  used,  pay  scales,  overtime  pay con-
straints,  land value  constraints,  equipment
and  facility  amortization  policy, and  social
and esthetic  considerations.

FINDINGS:   A practical  model for facility lo-
cation  has been  developed and used to de-
termine  optimal  locations.  Investigation of
sensitivity shows little  change in results  due
                                                                                       55

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to most parameter variations but a very great
sensitivity to volume of waste generated.
  A model  for optimal vehicle  routing has
also been developed. This model is not prac-
tical for realistic routing problems.
               PUBLICATIONS
REVELLE, C., D. MARKS, and J. C. LIEBMAN. An analysis
of  private  and public  sector  location  models. Manage-
ment Science, 16(11):692-707, July 1970.
         Mathematical Simulation of Refuse Collection and  Disposal Systems
                      Dr. Abraham Charnes
              Department of Geography and
                    Northwestern University
                   Evanston,  Illinois   60201
 Grant  No.  Ul 00699-04
 Funds Awarded: $75,067
 Project Period: Sept. 1, T962 to Sept. 30, 1967
OBJECTIVES:   To  develop  a  mathematical
model to simulate municipal refuse collection
and disposal practices.  It  will enable an  en-
gineer  to  predict the behavior of a  wide
variety of  proposed designs quickly and  ac-
curately and thus  to  predict  an  optimum
solution based upon more  complex criteria
than have  been possible.

APPROACH:  Data  were  first  collected  and
analyzed in  relation to  costs of refuse col-
lection and disposal unit  operations and  the
expected type and  amount of pollution  re-
sulting from  these  operations.  From this, a
comprehensive cost  function for each of  the
operations  involved was determined.  Mathe-
matical models were then formulated  to  de-
scribe  current refuse collection  and disposal
practices. Variables incorporated into the col-
lection system model .included  the  physical
characteristics of the refuse, storage facilities,
frequency  and type of pickup, capacity of  the
collection vehicles, collection time and  labor
costs, characteristics of the  haul to the dis-
posal site,  and the overnight garage location
of the collection vehicles. The use of transfer
stations was considered as well as the use of
more than one disposal operation. Variables
included in the disposal operation model  in-
cluded  the possibility of  salvage operations,
reclamation  possibilities,  direct cost factors,
the contribution of the disposal practices to
air and water pollution and to  reduction in
land  values, and  benefits  derived from  re-
claimed land.
FINDINGS:  Part 1 of this research began with
consideration of problems,  called  "location-
allocation" problems, in which several disposal
sites  were physically located with simulta-
neous allocation of refuse sources to disposal
sites.  The disposal  sites  were  located  any-
where in a plane,  and the measure of effec-
tiveness  was  minimization of aggregate haul
distance.  By  measuring distance with  the el-
metric  three things were accomplished,  as
follows.
   1. It was possible to  reduce these ei-metric
location-allocation problems to mixed-integer
programming problems.
   2.  Using the mixed-integer programming
formulation,  one may  add constraints  that
prescribe certain areas for the placement  of
disposal  sites.
   3.  The single-site  location problem  has  a
closed-form solution  related to the  geometric
median  of the  source  points. By using this
property, a Theory  of  Median  Sets was es-
tablished and an alternating location-alloca-
tion algorithm was constructed for the multi-
site problem.
   A second class of problems called "selection-
allocation" problems was denned.  Here the
set of  eligible  disposal site  locations was
known, and  one picked a proper  subset  of
these  and a refuse source allocation that mini-
mized the aggregate haul distance or cost.
These problems were characterized  as mixed-
integer programming problems with a coupled
network  analog and an  approximating al-
gorithm, and the Minimum Elimination Gain
56

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Algorithm  was established.' This  algorithm
was  extended  to consider weighted  sources
and site acquisition costs. The network analog
was  extended  to  consider site acquisition,
facility development, and  operation costs  as
well as aggregate  haul cost.
  Part 2 of this research traced the develop-
ment of  two  computer simulation  models.
The first model was  based  on the daily route
method of  refuse collection practiced in the
village of Winnetka, Illinois.  With data rele-
vant to Winnetka, a  series  of simulation runs
was made to delineate the interdependencies
of parameters involved in  the functioning  of
a refuse collection system.  In particular, the
percent of  truck  capacity  used, the  number
of daily trips, the overall collection efficiency,
the  length  of workday, the  haul efficiency,
and  the haul  time as a percentage  of total
time  were  measured as functions  of  the co-
efficient  of  variability of  refuse production,
the refuse assignment, and one-way haul dis-
tance. A further set of runs studied the effect
of the  number of  unloading  platforms on
average and maximum waiting times at the
disposal  site. The interpretation of  the re-
sults  presented  in tables and  graphs allowed
numerical  bounds on the usefulness of the
daily route method to be  established regard-
ing  the  coefficient of variability, the refuse
assignment, and haul distance.
  The second model was based  on constant-
length workday  rules  found  in  Chicago, Il-
linois. With data relevant to Chicago, a series
of runs was made  to measure the quality of
service and cost effectiveness of different com-
binations  of  overtime,  last-load relay,  and
assignment policy.  Here assignment  means
both  the average daily number of truckloads
and the average daily number  of 8-hour shifts.
The  results presented  in  a  series  of tables
show as one example that the  use of overtime
is most cost effective when  combined  with  a
reasonable  time  assignment.

                PUBLICATIONS

QUON, J. E., A.  CHARNES, and S. J.  WERSAN.  Simulation
and analyses  of  a refuse collection  system. Journal  of
the  Sanitary Engineering Division, American Society  of
Civil Engineers,  91 (SA5):17-36, Oct.  1965.
QUON, J. E., M.  TANAKA, and  A. CHARNES. Refuse quan-
tities and frequency of  service. Journal  of the Sanitaiy
Engineering  Division, American  Society of Civil  Engi-
neers,  94(SA2):403-420. Apr.  1968.

CHARNES, A., and W. M. RAIKE. One-pass algorithms for
some  generalized network problems. Operations  Re-
search, 14(5):914-924, Sept.-Oct.  1966.
CHARNES, A., and K. KORTANEK. A note on the discrete
maximum principle  and distribution problems. Journal
of Mathematics and  Physics, 45 (1):121-126, Mar. 1966.
QUON, J. E., M.  TANAKA, and S. J.  WERSAN.  Simulation
model of refuse  collection policies. Journal of the Sani-
tary  Engineering Division, American  Society  of  Civil
Engineers, 95 (SA3):575-592, June 1969.
                      Optimal  Policies  for  Solid Waste Collection
                      Dr.  Cornelius W.  Kruse
               Department of Geography and
                  Environmental  Engineering
                The Johns Hopkins University
                 Baltimore, Maryland  21205
  Grant No. Ul 00539-01
  Funds Awarded: $56,018
  Project Period: Jan. 1, 1967 to Dec.  31,  1968
 OBJECTIVES:  To  study  the  feasibility  and
 economics  of establishing transfer  points  in
 waste  collection systems  of large cities.  To
 devise, through  a  computer-oriented systems
 analysis study, more efficient use of manpower
 and equipment.

 APPROACH:   This  study  developed  informa-
 tion concerning  the characteristics of optimal
policies  for  use in urban decisions  by engi-
neers  and  municipal  decision  and  policy
makers.  A mathematical model  based on data
available  from  the city  of  Baltimore was
simulated to investigate the location and spac-
ing  of  transfer stations.  Problems  such  as
crew  size,  frequency  of  collection,  vehicle
routing, and type of equipment were analyzed.
   The study prepared  and programmed three
                                                                                           57

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mathematical  models of FORTRAN  IV for
use in digital computers. The models simu-
lated  the operations of solid waste collection
systems in urban residential areas using com-
pactor  trucks. Proposed policy  changes  in
a  system  can  be evaluated  by  use  of the
model rather  than by changes in  actual field
operations.
   The system variables that can be controlled
in some or  all of the models are  the  follow-
ing: density of households per acre, haul dis-
tances from neighborhoods  to disposal site,
truck crew, crew size, collection  frequency,
pay  scales,  overtime  policy,  amortization
policy,  season, use or nonuse  of a transfer
station, size of transfer station  trailers, use
or nonuse  of  transfer station compaction ap-
paratus, haul  distances from transfer stations
to disposal site, and use or nonuse of  queues
at transfer stations.
   The  relative efficiencies of the  systems be-
ing compared  were  measured  in dollars-
per-ton-costs.  Costs  of residential  triweekly
collection versus biweekly collection were com-
pared. For a particular urban tract with the
controllable variables defined, the model gen-
erated the number of collection  trucks  by
number and by days to areas within the tract.
  The combinations of variables that make
the  use  of a  transfer station  economically
desirable were investigated.

FINDINGS:  The final  model  (Model III)  is
suitable  for use by any city in investigating
system changes.
  For the area of Baltimore investigated, the
break-even haul distance for a transfer station
is about 8 miles.  Auxiliary compaction  is a
marginal operation. Increasing collection fre-
quency from  two  to three per week results
in a 10 to 15 percent cost increase.
               PUBLICATIONS

TRUITT, M. M., J. C.  LIEBMAN, and C. W. KRUSE. Simula-
tion model  of urban refuse collection. Journal  of the
Sanitary Engineering  Division, American Society of Civil
Engineers, 95(SA2):289-298, Apr. 1969.
             The  Physical  and Chemical Composition of Municipal  Refuse
                    Prof.  Don t.  Bloodgood
            Department of Civil Engineering
                          Purdue University
                  Lafayette,  Indiana   47907
  Grant No. EF 00146-05
  Funds Awarded: $84,165
  Project Period: Sept. 1, 1957 to Dec. 31, 1962
OBJECTIVES:   To develop physical and chemi-
cal methods of sampling and analyzing mu-
nicipal refuse. To determine the amount  of
solid waste generated and  its characteristics.

APPROACH:  Field studies were conducted  in
seven major Midwestern cities to obtain sam-
ples of refuse  for laboratory analysis and  to
determine the amounts generated from differ-
ent  socioeconomic neighborhoods. The sam-
pling methodology was evaluated.
   Laboratory studies were  conducted  to de-
termine the error due  to two necessary sam-
pling  stages of the  collected refuse before
chemical analyses. Laboratory studies included
the development  of reliable  methods of de-
termining the following tests on municipal
refuse:  moisture,  lipids,  carbon,  nitrogen,
K2O, P2Os, sulfur, and calorific  value.

FINDINGS:  The determination of the param-
eters  of Ib per capita per day, Ib per house-
hold  per  day, cu  ft per capita per day, and
bulk  density for a "homogeneous" residential
area within a community required a sample
of approximately  175 households for obtain-
ing accuracies within 10 percent of the mean
from the mean at a confidence  level of 95
percent.
  On the basis of more than 2,400 samples ob-
58

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tained from Milwaukee, Wisconsin; Toledo,
Ohio;  and  Bloomington  and  Indianapolis,
Indiana, it  was determined that significant
differences exist in the quantity and quality
of the refuse produced in high, medium, and
low socioeconomic sections of the cities.
  On  the basis of  more than  65 separate
studies  in these four  cities, the  following
logarithmic relationship was found between
the sampling  ratio   (population  of sample
areas  divided  by total city population) used
and the percent sampling error (percent error
between extrapolation of sample data to esti-
mate  total city  production and actual total
city production):
                       -°-781x
    where  Y resampling ratio, expressed as
                 a decimal
            X— percent sampling error
            e —base of natural logarithm
    NOTE:  It is recommended that at  least
    400 people  be  used as  a total  sample
    population  when a refuse sampling study
    is conducted.
  The  following procedure  for  processing
samples of  refuse before laboratory analysis
is recommended:
    Shred combustible portion of the refuse
    with  a forage  harvester to a  maximum
    size of 2 to  3 in. Select a "representative"
    sample of from 1,000 to 3,000 g and de-
    termine the moisture  content by drying
    in a forced-air oven at 70 C. Grind dried
    material  in a  standard  laboratory-type
    Wiley Mill to a maximum size of 2 mm.
    Store  in  an airtight,  labeled can until
    needed for  subsequent chemical analysis.
  This sampling step,  plus the  sampling of
the material in the airtight can for as little as
2 g in some  cases,  was found to have the
following overall sampling error:
  1. One has 95 percent confidence  that, if
only one sample is selected from the initially
shredded  paper material, and  this sample is,
in turn, subsampled after drying and grinding
to obtain  a final aliquot for a chemical deter-
mination, the overall sampling error will not
exceed  10.3 percent.
  2. One has 95 percent confidence  that, if
only one sample is selected from the initially
shredded  garbage material,  and  this is,  in
turn,  subsampled  after drying and  grinding
to obtain a final aliquot for a chemical deter-
mination, the overall sampling error will not
exceed 7.2 percent.
  Recommended methods of chemical anal-
yses  for  the combustible  portion of refuse
were  developed during the project  for mois-
ture,  volatile solids,  ash, lipids, liquid con-
tent, sulfur, nitrogen, carbon, hydrogen, C/N,
P2O5, K2O, and calorific value.
  The following "empirical factors" were de-
veloped for the determination of carbon  and
hydrogen of garbage, remaining combustibles,
and total  combustibles of a refuse:
  Raw garbage:   % C = (100—% Ash)/1.97
                  % H = (100-% Ash)/12.8
   Remaining     % C = (100—% Ash)/2.18
    combustibles:  % H = (100—% Ash)/14.7
  Total           % C = (100—% Ash)/2.08
    combustibles:  % H = (100—% Ash)/14.4
   A  special  study in Indianapolis, Indiana,
where the people do a great deal of backyard
incineration, showed the following findings.
   1.  If the people were  asked to  put out all
their  refuse, an increase from  3.4 to 8.3 mil-
lion  Ib and from 4.0 to 5.2 million Ib of
refuse per week could be expected in Decem-
ber and  August, respectively.
   2.  If the  people were required, by  ordi-
nance, to put out all their refuse,  an increase
from  3.4 to  10.6 and from 4.0 to  7.4 million
Ib of refuse per week could be expected in
December and August, respectively.
   The results  of a questionnaire  in the 119
cities having  a population of  more  than
100,000 in the United States (1958)  indicated
that:
   1. Only 3.3 percent of 95 of the larger cities
in the United  States  conduct refuse-sampling
procedures on  a routine basis.
   2. Only 19 percent of 95 of the larger cities
in the United States have their own laboratory
facilities for determining either ash content
or moisture content.
   3. Only 9.5 percent of 95 of the larger cities
in the United States have their own laboratory
facilities for refuse grinding or determination
of calorific value.
                                                                                       59

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               PUBLICATIONS

BELL, J. M. The physical and chemical composition of
municipal  refuse.  The  APWA Reporter, 29(1):11, Jan.
1962.

ETZEL, J. E., and J. M. BELL. Methods of sampling and
analyzing refuse. The.APWA ^Reporter, 29(ll):2-4, 18-21,
Nov. 1962.

BELL, J. M. Characteristics of municipal refuse. In  Pro-
ceedings,  National Conference of Solid Waste Research,
Chicago,  Dec. 1963,  University  of Chicago  Center  for
Continuing Education. Special Report No. 29. American
Public Works Association,  1964. p. 28.
                 Comprehensive Studies  of Solid Waste  Management
                    Dr.  Clarence G. Golueke
   Sanitary Engineering  Research  Laboratory
           University of California—Berkeley
                 Berkeley, California  94720
  Grant No. EC 00260-04
  Funds Awarded: $792,822
  Project  Period:  June 1, 1966 to May 31, 1970
OBJECTIVES:   To develop  an overall  system
by which the economic, administrative, plan-
ning, land use, logistic, technologic, engineer-
ing,  health,  and  waste-generating aspects of
the solid waste problem of a community or
region can be evaluated in designing a waste
management  scheme for that area.

APPROACH:   A number of research teams in-
vestigated the various aspects of solid waste
management, including operations  research,
planning and economics,  public health,  and
technology.
   The operations research team  developed an
overall solid wastes generation and evaluation
model. This model  included constituent sub-
models that interrelated land use, technologic,
economic, population, transport, and all other
aspects of solid waste  management. The time
horizon  for  the overall model was 20 to 50
years. The planning and economics team re-
lated land use  to the nature and volume of
refuse materials to be  handled, with  major
emphasis on  the ultimate disposal  of  wastes.
The  public  health  team evaluated  the rela-
tionship  between  solid waste  management
procedures and health dangers to the  public
and  advised  the other research  teams  on the
possible  public health  implications of their
alternate proposals  for waste management.
   The research teams concerned with tech-
nology,  investigated many processes, includ-
ing anaerobic digestion and sludge processing,
and   pyrolysis—combvistion,  wet  oxidation,
and biological fractionation. The underlying
principle  of the  anaerobic  digestion  and
sludge-processing scheme was  the assumption
that various organic fractions of solid waste
can conceivably be transported  to  a  sewage
treatment plant either via  water carriage or
by trucks. If this mixed organic matter could
be digested anaerobically,  it would  be  re-
duced in volume and at the same time condi-
tioned so as to minimize its insult to receiving
land. A pilot plant was built to digest  anaero-
bically  a solid  waste-sewage sludge mixture,
and the operational parameters  developed in
laboratory studies were refined. The pyrolysis-
combustion  process is  one  in which  organic
matter is converted to combustible gases, and
the gases are, in turn, burned to produce heat.
Pilot-plant studies developed techniques  for
using various types of wastes as a fuel  for the
pyrolysis-combustion process.  The  pyrolytic
gases produced were used for sustaining the
process and as  a source of energy  to be re-
cycled to the industry  and community  pro-
ducing the wastes. Laboratory and pilot-scale
research  investigated the  possibility of using
a  wet-oxidation process to convert all  but the
most exotic synthetic organic compounds to
simple  oxidation products  having industrial
value. Organic  chemical yields  were deter-
mined  and  the various  chemicals  produced
were identified.  Biological fractionation stud-
ies centered around the enzymatic hydrolysis
of the cellulosic portion of solid waste  to form
glucose.  Laboratory and pilot-scale  investiga-
 60

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tions  were  made to optimize the  glucose
production.

FINDINGS:   In the first stages of the research
an overall waste management model  was de-
veloped in which the final output was a "waste
collection,  treatment,  and disposal"  compo-
nent.  Components  of the  model  serving  as
inputs to the final component were "regional
economic," "waste generator,"  "interregional
analysis," "national economic," "population,"
"process technology," "spatial distribution of
wastes," "land use," and "public health." The
framework of the model having  been  estab-
lished,  the subsequent efforts  were devoted
to collecting data and formulating inputs for
the various components  of the model. Major
progress was  made in establishing  the waste
generator, spatial distribution of wastes, land
use,  process  technology, and  public  health
models.
  Public health.  By means of five extensive
tables, data on the types and composition of
solid  wastes and  the  fate of  the components
of their breakdown products were  screened
and evaluated; as a result of  this activity, the
fractions of the solid waste stream that might
have  public  health significance were  identi-
fied. The  public health significance and en-
vironmental  fate of the various  fractions in
relation to wastes processing  or disposal were
evaluated. Means were suggested  for keeping
those  components shown to  constitute a sig-
nificant hazard  from  entering the  environ-
ment  in such a manner as to come in contact
with  man. One of the major conclusions of
the public health aspects of the research was
that at present there is more need for research
teams  on  which public  health specialists are
prominent contributors  along  with scientists
and  technologists than  for  specific  health-
oriented studies.
  Planning and economics. The planning and
economics study  led  to  the  development  of
the concept of functional boundaries  and to
the formulation of waste multipliers based on
type of economic  and demographic activity.
In line with this approach, it was found that
the traditional 4 to 6 Ib/capita waste  figure
was far below the amount of wastes actually
generated.  The research team showed that
the amount of solid wastes handled at landfill
disposal sites was only about 50  percent of
the total solid wastes production. This finding
was confirmed later by studies conducted by
the California State Department  of  Health.
The work was later expanded  to  include  a
study of related  aspects of the solid wastes
management problem, such as the questions
of local versus  regional  solution, alternate
pricing systems, and development of efficiency
versus equity criteria.  During  the research,
network flow models were developed for the
efficient rerouting of solid wastes from origin
to sites; an  economic  survey was made  of
engineering aspects of current and experi-
mental  technologies' disposal costs.
   Operations  research. The  operations re-
search group developed a solid waste regional
forecasting model in which the 28 sectors in
the 9-county San  Francisco Bay region  were
recognized.  One  of the novel features of the
model is its ability to forecast waste genera-
tion for large communities.  The  procedure
used in developing the model was based on
the Leontief input-output model.
   This portion  of the study was concerned
with  the  development of a model showing
optimal service policies for solid waste treat-
ment facilities. In the approximate version of
the problem, the cost structure was described
by a quadratic processing  cost rate charged at
the end of each  period, and a linear  holding
cost charged at the end of  each period.  The
arrival  stream was considered to  be period-
ically interrupted and divided into alternat-
ing "on"  and "off" intervals of fixed length.
The distribution of the cumulative quantity
of waste that arrives during each "on" interval
was represented  by its first two moments. No
wastes were assumed to come into the  proc-
essing facility during each "off" period.  The
optimal service rates were found to be linear
in the waste level at the start of each  "on"
interval and piecewise linear  in the quantity
of waste  present  at the  start of  each  "off"
period.
   Anaerobic digestion. In  accordance  with
the exploratory  nature of  objectives  of the
anaerobic digestion studies,  experiments  were
concerned  with  the effect  on the digestion
process  of adding the  various ingredients of
typical  refuse to  the  input to  the digester.
Thus,  it was found that once a digester cul-
                                                                                       61

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ture is  adapted to using green  garbage as a
substrate, it can  digest  the  garbage  as  effi-
ciently  as it does raw  sewage sludge,  and at
about 90 percent of the gas production from
sludge  digestion. More  than 90  percent of
the cellulose added  as Kraft paper was  di-
gested.   Newspaper (as  found  in  domestic
wastes)  was only about one-half as digestible
as Kraft or  raw sewage sludge. Garden debris
was digested at a rate  and extent equivalent
to those of  garbage or sludge but with a  gas
production  equal to only  75 percent of  the
latter. Wood was virtually unchanged in  the
digestion process. A  composite of all  the in-
gredients of domestic  refuse  was  digested at
solids destruction efficiency of about  65  per-
cent.  Gas production was about 63 percent of
that obtained from digesting an equal amount
of sewage sludge. During the study, a kinetic
model of the anaerobic biologic hydrolysis of
cellulose was  developed by  one of  the  re-
searchers as a  part of his work on a doctoral
dissertation. An  economic  analysis  showed
that the total costs (1960 dollars) for digesting
municipal refuse would be  about $2.18/ton
for a city of 300,000, and  0.78/ton for a city
of  1 million.
   Wet  oxidation. A  wet-oxidation unit ca-
pable  of treating 40  liters  of slurry on  a
"batch" basis or of being operated on a  con-
tinuous basis was constructed and used in pre-
liminary experiments.  In  these experiments,
the reaction temperature was varied from  160
to 220 C in 20-degree increments,  and air was
applied at  1  to 2 cu ft/min.  Air  (partial)
pressure was raised to  180 psia. Under these
conditions  maximum  dissolved  solids yield
(i.e., maximum total organic chemical yield)
was about 35 percent of the total solids input.
Residual solids yields  decreased to some  ex-
tent  and volatized carbon  yields increased
with  temperature increase;   dissolved solids
yields increased with temperature until a max-
imum was  reached,  after  which  they began
to  decline.  Residual  solids  and  volatilized
carbon  yields were smaller and dissolved solids
yield was greater for every 2  cu ft of air  per
minute  at  every reaction  temperature. The
cellulosic fraction of wood is preferentially at-
tacked under acidic conditions. Organic chem-
icals  produced in the  reactions  were those
from  oxidative degradation of the component
pentose and lexose manomers  of  wood, e.g.,
acetic, formic, lactic, glycolic, and other acids.
  Pyrolysis  combustion.  Work in  the  pyrol-
ysis-combustion studies was concerned mostly
with the design and construction of a reactor
capable of handling 200 Ib of refuse per hour.
The design  of  the reactor departs  from the
usual  pyrolysis  reactor  in  that  a limited
amount  of  combustion is provided to bring
the  temperature  of  the pyrolysis-produced
gases to 800 to  1,200 C. These gases are used
to bring the wall temperature of the pyrolysis
chamber to 800  to 1,200 C.  The operation of
the unit is  sufficiently flexible to permit  the
production  of useful intermediate breakdown
products or to carry the destruction process to
a point  at  which  only  CO2, H2O,  and inert
ash need be discharged to the environment.
  Biofractionation. The  work done on bio-
fractionation led  to  the development of  a
fermentation geared to  the  optimum  condi-
tions for the biological hydrolysis of cellulose
to glucose and the culture of a potential feed-
stuff on the glucose. A number of  organisms
were surveyed.  The one found most suited to
the  process was  the  fungus  Tricho derma
viride.
   General.  During the  research  period,  the
pertinent literature was extensively covered—
more  than  700 publications were reviewed
and abstracted. This activity led  to the pub-
lication  of two  highly useful reports. A third
is being  compiled. When it is finished,  the
number of  publications thus reviewed will
number more  than 1,000.
                PUBLICATIONS

 GOLUEKE, C. G., and P. H. MCGAUHEY. Future alterna-
 tives to incineration and their air pollution potential. In
 Proceedings; Third National Conference on Air Pollution,
 Washington, D.C., Dec.  12-14,  1966,  National  Center
 for Air Pollution  Control, Public  Health Service, U.S.
 Government Printing Office, 1967. p. 296.

 MCGAUHEY, P. H. Living with our wastes. In J. E. Flack,
 and M. C.  Shipley, eds. Proceedings; Ninth Western Re-
 sources Conference, Man and the  Quality of His Environ-
 ment, University of Colorado,  Boulder, July 5, 1967.
 University of Colorado Press, 1968.

 GOLUEKE, C. G. Comprehensive studies on waste manage-
 ment. Presented  at Engineering Foundation Research
 Conference, Solid Waste Research and Development, Uni-
 versity School, Milwaukee, July 24-28,  1967.  Conference
 Preprint No. A-l. 3 p.
 62

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GOLUEKE, C. G., and P.  H1.  MCGAUHEY. Comprehensive
studies of solid waste management; first and second an-
nual reports. Public Health Service Publication No. 2039.
Washington, U.S. Government Printing Office, 1970. 245 p.

GOLUEKE, C. G.  Solid waste  management: abstracts and
excerpts from the  literature,  v. 1 and 2. Public Health
Service Publication No.  2038. Washington, U.S. Govern-
ment Printing Office, 1970. 147 p.

ANDERSON, L. E. Comprehensive studies of solid  wastes
management; a mathematical model for the optimization
of a wastes management system. Rev.  by  A. K. Nigam.
SERL Report No. 68-1. Berkeley, University of California,
Feb. 1968. 63 p.
STERN, H. I. Comprehensive studies of solid wastes man-
agement; optimal service policies for solid waste treat-
ment facilities. SERL  Report No. 69-6. Berkeley,  Uni-
versity of California, May 1969. [139 p.]

GOLUEKE, C. G. Chemical and microbial  characteristics of
urban solid wastes. [Presented at Annual Meeting, Amer-
can Society  for  Microbiology, Miami Beach, May 4—9,
1969.] 17 p.

BRINK, D. L., P. K. BASU, and J. F. THOMAS. Pyrolysis—
combustion:  a new type of recovery system. Unpublished
data, Department of Forestry and Conservation, Univer-
sity of California, Berkeley, 1970.
                       Decision Making  and Solid  Waste  Disposal
                         Dr. John R. Shectffer
                    Center for Urban Studies
                       University  of Chicago
                     Chicago, Illinois  60637
 Grant No. EC 00281-02
 Funds Awarded: $201,008
 Project Period: Mar.  1, 1969 to Feb. 28, 1971
OBJECTIVES:  To  measure the  influences  of
economics in solid waste disposal and to for-
mulate methods of using economic analysis as
a guide in designing  facilities,  including at-
tention  to costs of alternative  technologies.
To identify the factors initiating, supporting,
opposing,  and negotiating refuse disposal de-
cisions and  to  classify and analyze areas  of
interaction.  To  determine the  nature  and
extent of short-run opinion changes by local
people and  to  develop education approaches
that may be desirable  to decrease aversions to
location of facilities.

APPROACH:  Various solid waste management
methods, i.e., landfills, incineration, compost-
ing, and  so  forth,  are being  compared  to
determine conditions  under  which different
cities  may find cost advantages  in particular
technologies. An  attempt is  being made  to
understand  cost  variations  and to separate
out the extent  to  which these are due to dif-
ferences in land and  labor costs, differences
in  techniques  of  disposal used,  and differ-
ences  in efficiency. The efficiency  of private
companies  and  of public  agencies is  being
compared. The effect of existing  regulations
on  private waste disposal  is being evaluated.
Hypotheses are being  formulated and investi-
gated about policy approaches involving regu-
lation, financing, pricing, and other measures
aimed at ensuring arrangements that will be
conducive  to waste  disposal procedures per-
mitting  maximum attainment of goals.
   A decision-making framework was  formu-
lated from  empirical data and theoretical con-
cepts.  Selected decisions about  the location
of solid  waste disposal  sites were analyzed to
provide  basic empirical data.  Physical and
social  factors, including those often termed
political, were considered.  Eighteen requests
for permission to operate sites for the disposal
of solid  wastes were analyzed. Of the 18 cases,
5  are instances of rail  haul while  the  others
involve  truck transfer  to  sanitary landfills.
The significant factors were identified and re-
lated to the  socioeconomic situations  of the
community in which the decisions were made.
   At the same time,  two rail haul proposals
were analyzed with an emphasis on  under-
standing the social  psychologic  factors  that
affect protest. Ethnographic information and
personality factors leading to certain attitudes,
attitude  changes, and willingness to act are
being investigated.

FINDINGS:   Much progress  has been made in
the development of an  economic framework
                                                                                            63

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for analyzing  solid waste disposal  consistent
with a constructive  use of  resources instead
of a negative destruction and  riddance ap-
proach.  Major components  of the economics
of solid wastes as a field of inquiry have been
identified,  including classification of various
waste disposal activities  and delineation of
subjects of inquiry ranging from elementary
cost  comparisons, to more sophisticated  com-
parisons, to the  analysis of solid  waste  dis-
posal systems, to the economic  evaluation of
institutional arrangements,  and  to legal  and
policy areas. For all but the legal and policy
areas, substantial progress has been made in
developing conceptual  frameworks  to  guide
our own and other people's efforts. This work
is being continued.  Also being  continued is
the empirical  work  on  demand for disposing
of wastes;  on the analysis  of  cost  function,
including  design  of needed  data  collection
systems; and on the evaluation of entire waste
disposal systems.
   An important factor  in  planning future
solid waste management is the volume of
refuse expected  to accrue in later periods, as
well as  its composition. To obtain estimates
of future solid waste figures, one could simply
extrapolate the  trend observed in  the  past.
One might, however, be caught by surprise
when so doing, since new trends become pre-
dominant that were not apparent  in global
figures but that would have been detected by
a more careful analysis of the data.
   For a statistical cost analysis of solid waste
disposal, multiple regressions were  based on
National Survey data. Although  this approach
was successful in depicting cost  functions for
municipal  incinerators,  it  did  not do  very
well for small incinerators and landfills.  This
is probably due to data deficiencies, and one
main conclusion from our work so far is  that
a major effort must  be undertaken  to collect
better data. In view of this, normative  cost
accounting  sheets have been  developed. If
adopted by managerial personnel, they would
ensure that cost items would be reported in
a standardized way  to yield meaningful  cost
information.   These  are  prerequisite for a
rigorous economic analysis as needed for plan-
ning future solid waste  management.
   From the site proposals studied  a number
of important factors were found. By construct-
ing a series of matrices, factors such as visibil-
ity  of a site, lower status of the community
involved,  the mayoral  form of government,
and reclamation were found to be positively
related to acceptance of sites. Factors such as
a perceptible reclamation, site size, and dis-
tance from a site to the nearest residence were
found  to  involve some important qualifica-
tions. Reclamation was found to be positively
related to acceptance of a site but apparently
had little  effect on whether or not significant
protest took  place. Size of a site and its dura-
tion were not found to be positively related
to acceptance of a site. Factors  such as dis-
tances  were  found  to vary considerably. A
community typology  consisting of four  types
was developed.
     Type  I—incorporated  area  for  a single
       community—three proposals—all suc-
       cessful
     Type  II—outside the region for a single
       community—five proposals—all unsuc-
       cessful
     Type  III—incorporated area  for multi-
       ple  communities—one  proposal—suc-
       cessful
     Type IV—within the region for multiple
       communities—nine proposals—six suc-
       cessful, three unsuccessful
  If one considers the eight communities with
urban  settings and middle to high status, pro-
test was significant  after the public hearing
in only three, and seven of the eight proposals
were ultimately implemented. In the remain-
ing  seven  communities with lower status or
with rural or isolated settings, only  three of
the  proposals  succeeded  and  all  were  pro-
tested. But protest is most effective  in  cases
of the  Type  II variety where a single commu-
nity transports its refuse outside  the region.
Although there is a tendency to go toward
the areas where there is a great deal of open
space with as few residents as possible, per-
haps more is lost in this strategy than gained.
Because of the  township system there  is no
area in which  the local community gives up
its jurisdiction except for those without zon-
ing and zoning ordinances. As was very clear
in the rural  or  isolated communities studied
thus far, the proportion of citizens protesting
in these areas was vastly more significant than
in urban  areas. In fact, their absolute  num-
64

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her was almost  always  high'er. Not only did
such  communities  see  themselves as highly
self-sufficient with regard to disposal, but also
some economic  changes that were likely to
occur there would be  significantly different
than  they might have been elsewhere.
  In  Denver, San Francisco, and possibly in
Milwaukee, rail haul does not appear to be
able  to compete with  systems incorporating
truck  transfer.  Intergovernmental  arrange-
ments are  indicated as having added to the
planning problems—it is difficult to get all
necessary contracts  in line in a metropolitan
area.  Finally, the  specific  problems  of rail
haul  parallel  the general problem of misin-
formation  that  has characterized solid waste
disposal  efforts.  For example,  Philadelphia
was  cited  in  the  San  Francisco  proposal as
evidence of the success of the rail haul  con-
cept.  Its concept has not yet,  however,  gone
into operation. Another example of misinfor-
mation is that the published cost estimates of
rail haul systems indicate that some are going
to reap unbelievably  large  profits or  that
others are  going to sustain colossal losses.
  In  the social  psychology work,  personality
factors  leading  to certain attitudes, attitude
changes, and  willingness to act were  investi-
gated. Sex  differences were observed;  women
changed more often and to  a greater extent
than  males. In addition, a number of factors
such  as trust in public officials, trust in the
private operators, and  previous community
changes were  identified as important in the
decision. Other factors such as distrust toward
outside agents were also found to be impor-
tant. Among those who are more fearful and
apprehensive and who tend to avoid risks (the
harm-avoidance  scale), those who favored the
proposal  before the  discussion  were  more
willing to act  than  those who  opposed it,
while  those xvho  favored  the  proposal  after
the discussion were less willing  to act than
those who opposed it. In other words, the
propensity to take risks was associated with
willingness to act if one was negative to the
landfill before the discussion and if one was
positive  to  the  landfill after the discussion.
This  suggests either  that  individuals who
were  originally  riskier and more willing to
act shifted from a negative to a positive atti-
tude or that the discussion made the risks in-
volved in the landfill more salient and thus
increased the  negative  relation between will-
ingness to act  in  favor of the landfill and
harm avoidance and the amount of attitude
change, whether positive  or negative. These
findings  are not satisfactorily explained, but
they do  suggest that distinctive appeals will
be  successful  in motivating opposing groups
in a landfill controversy.

                PUBLICATIONS

HAVLICEK,  J., JR., G.  S. TOLLEV, and  Y. WANG. "Solid
wastes"—a resource? American Journal of  Agricultural
Economics, 51(5):1598-1602,  Dec.  1969.
                 Standard Test Procedures  for Municipal Solid  Wastes
                       Dr. Russell H. Susag
    Department of Environmental Engineering
                        University of Florida
                 Gainesville, Florida   32601
 Grant No. EC 00332-01
 Funds Awarded: $38,887
 Project Period: June  1, 1969 to May 31, 1972
OBJECTIVES:   To  develop standard test  pro-
cedures for the physical, chemical, and  bio-
logical  characterization of  municipal  solid
wastes. This information will implement bet-
ter design, operation, and environmental  con-
trol of the collection, storage, transport, proc-
essing, and disposal of municipal solid wastes.
APPROACH:   Presently  used  test procedures
for the examination of municipal solid wastes,
as well as recommendations for other desired
analysis,  are being investigated by means of a
questionnaire survey sent to people and agen-
cies involved in solid waste management. An
Advisory Committee  on Test Procedures for
                                                                                        65

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Municipal Solid Wastes is being formed from
representatives of the  agencies surveyed and
through  technical associations and  societies.
This  committee would provide  the broad
base for  direction in standardization  of test
procedures and  dissemination of information
through  the  constituent societies.  Personal
contact and an extensive literature search are
also being made.
  These  existing procedures will be evalu-
ated through  consultation with the agencies
and actual  performance  of  the test  for ac-
curacy, precision, reproducibility,  and appro-
priateness.  Sampling procedures and  sample
preparation are also  being  investigated  so
that the  representativeness  of samples taken
from extremely heterogeneous municipal solid
waste can be  ascertained.
  As  a result of this  work, shortcomings of
existing  methods and  recommendations for
improving them can be delineated.

FINDINGS:  A  survey of the State's solid waste
planning directors indicated that their activi-
ties have been confined to solid waste plan-
ning and quantitative  data  gathering. Very
little qualitative analysis is being performed.
The need for a set of standard test procedures
for solid waste analysis was,  however, recog-
nized and encouraged. A literature review in-
dicates that test procedures for the examina-
tion of  refuse  have  been  borrowed from
Standard  Methods for the  Examination of
Water and  Wastewater, ASTM, and AOAC.
Researchers at several  universities have de-
veloped  or revised existing  analysis proce-
dures  to  meet project objectives, the  most
extensive work being in the  area of incinera-
tor residue characterization at Drexel Univer-
sity, Harvard University, and New York Uni-
versity. The BSWM intramural forces  have
done extensive work in the area of sampling
and sample preparation  as  well  as  in the
development of specific analytical procedures.
These  methods   are  being  compiled  for
evaluation.
             Biologic Consequences of Plant Residue Decomposition in Soil
                      Dr. William C. Snyder
              Department of Plant Pathology
            University  of California—Berkeley
                 Berkeley, California 94720
  Grant No. EC 00267-06
  Funds Awarded: $211,779
  Project Period:  Feb. 1,  1964 to Mar. 31, 1971
 OBJECTIVES:   To investigate and  determine
 the nature and action of phytotoxic substances
 released into  soils during plant residue deg-
 radation. To assess the biologic consequences
 arising from the decomposition products  on
 succeeding crops and their diseases.  To  as-
 certain the relationships between decompo-
 sition  products and types of plants and en-
 vironmental  factors. To evaluate  the  role of
 degradation products in the survival of patho-
 gens in soil and to determine the  nutritional
 requirements  for pathogenicity and the role
 of crop residues in providing such nutrients.

 APPROACH:  The plant organic-residue  sources
 are barley, rye, soybean,  timothy,  and other
common  plants—all  of which are  known
phytotoxin  producers  upon decomposition.
Phytotoxins are  obtained by extractive  pro-
cedures, and isolation and identification are
attempted by  use of chromotographic  and
chemical  techniques. Phytotoxicity assays are
run at the analytical separation stages by eval-
uation  of seed germination  and root  elonga-
tion.  After identification,  plant evaluation
studies  are made  in nutrient  culture  and
nonsterile soil growth conditions. The  per-
sistence and prevalence  are  determined for
the identical compounds in nature. Fusarium
and Thielaviopsis organisms are used to de-
termine the effect of  phytotoxins  on  their
parasitic activity in laboratory and whole-plant
 66

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greenhouse studies.  Soybean  and barley tis-
sue  at  various  stages of  decomposition  in
natural  soil under  controlled conditions is
assayed  for the  appearance and  duration of
production of  these  compounds.


FINDINGS:    Bioassays,  using  lettuce  and to-
bacco seed germination  and  root-elongation,
demonstrated  the phytotoxicity of water ex-
tracts of barley,  rye, broccoli,  and vetch resi-
dues decomposing in the  field. Four phenyl
acids were identified that accounted for much
(50  to 60  percent) of the phytotoxicity of the
extracts.
   In the  laboratory studies these  phytoxins
were shown to predispose hosts to Thielaviop-
sis root rot. During the work with Thielaviop-
sis the process of chlamydospore  germination
was  demonstrated. Residue-related damage to
lettuce seedlings in fields in the Salinas Valley
was  not correlated with  the phytotoxicity of
extracts from  decomposing residues  in  these
fields. Field and greenhouse  studies  showed
that incorporation of barley,  rye, or broccoli
residues into field soils consistently  increased
the  population density of  Pythium ultimum.
In the  first 3 to 4  weeks following  residue
incorporation  the   increased  population of
Pythium  ultimum  caused significantly  more
damping  off and root injury to lettuce  seed-
lings. Subsequently,  even though the P. ulti-
mum population remained greater in residue-
amended  soils, the degree of damage to lettuce
seedlings  was less than that observed  in non-
amended   soils.  The  residue-related  damage
observed  in the  field was due  to the effect of
the   residue on  pathogen  populations,  par-
ticularly  its utilization as a  substrate by P.
ultimum.
                 PUBLICATIONS

PATRICK, Z. A., T. A. TOUSSOUN, and L.  W. KOCH.  Effect
of  crop-residue  decomposition  products  on plant  roots.
In  Annual Review of phytopathology,  v. 2. Palo Alto,
Calif., Annual Reviews, Inc., 1964. p. 267.

PATRICK, Z. A.,  T.  A. TOUSSOUN,  and   H. J. THORPE.
Germination of  chlamydospores of Thielaviopsis basicola.
Phytopathology, 55(4):466-467,  Apr. 1965.

PATRICK, Z. A.,  R. M. SAYRE, and H.  J. THORPE.  Nema-
tocidal substances selective  for plant-parasitic  nematodes
in  extracts of decomposing rye.  Phytopathology,  55 (6):
702-704, June 1965.

SAYRE,  R.  M., and  Z. A.  PATRICK. Selective toxicity  of
some  volatile fatty  acids  to plant-parasitic nematodes.
Phytopathology, 55(10):1074, Oct. 1965.  (Abstract.)

LINDERMAN,  R.  G.,  and T. A. TOUSSOUN. Behavior  of
chlamydospores  and  endoconidia of  Thielaviopsis basicola
in  nonsterilized  soil.  Phytopathology, 57(7):729, July 1967.

LINDERMAN, R. G., and T.  A. TOUSSOUN. Pathogenesis of
Thielaviopsis basicola. Phytopathology, 57(10):1007, Oct.
1967.  (Abstract.)

LINDERMAN, R.  G., and T.  A. TOUSSOUN. Predisposition
to  Thielaviopsis root rot by phytotoxins obtained from
decomposing  plant  residues. Phytopathology, 57(8):819,
Aug. 1967. (Abstract.)

TOUSSOUN, T. A., A.  R. WEINHOLD, R. G. LINDERMAN, and
Z.  A.  PATRICK.  Identification of phytotoxins obtained
from plant residues  decomposing  in soil. Phytopathology,
57(8):834, Aug.  1967.  (Abstract.)

LINDERMAN, R.  G., and T.  A. TOUSSOUN. Breakdown in
Thielaviopsis basicola root  rot resistance in  cotton  by
hydrocinnamic  (3-phenylpropionic) acid. Phytopathology,
58(10):1431-1432, Oct. 1968.

LINDERMAN, R.  G.,  and T. A. TOUSSOUN. Predisposition
to Thielaviopsis root rot of cotton by phytotoxins from
decomposing  barley   residues.  Phytopathology,  58(11):
1571-1574, Nov. 1968.

LINDERMAN, R.  G., and T.  A. TOUSSOUN. Pathogenesis of
Thielaviopsis basicola  in nonsterile soil. Phytopathology,
58(12): 1578-1583, Dec.  1968.

WEINHOLD,  A.  R.,  T. BOWMAN, and  R.  L. DODMAN.
Virulence of Rhizoctonia solani as affected by nutrition
of  the pathogen. Phytopathology, 59(11): 1601-1605, Nov.
1969.
                                                                                                  67

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                              Pyrolysis of  Municipal  Refuse
                         Mr. Elmer R. Kaiser
        Department  of Chemical  Engineering
                       New  York  University
                   Bronx, New  York  10453
 Grant No. EC-00253-06
 Funds Awarded: $126,728
 Project Period: Sept.  1, 1963 to Feb. 28, 1970
OBJECTIVES:   To determine  the nature  and
quantity of the volatile matter resulting from
the  pyrolysis of  refuse  components.  To in-
vestigate  the  possibility of  recovering  and
using the combustible gases produced.

APPROACH:  Initially, a small laboratory fur-
nace was used to heat a closed retort charged
with a small  amount of  refuse components
such as  paper, garbage,  plastics,  fats,  oils,
waxes, wood, leaves,  and sewage sludge.  The
resulting products were analyzed both quali-
tatively   and  quantitatively.  The  calorific
values of the refuse input and pyrolytic out-
puts were determined.
  Later,  a  13.5-in. diameter by 5-ft  gasifier
was built and used to investigate the pyrolysis
process.  About 200  Ib of refuse per  hr was
pyrolyzed, and the output gases were collected
and analyzed. The variables studied included
feeding  rate,  rate  of residue  removal,  rate
of air supply,  temperature  and  humidity  of
the  air,  depth  of  refuse  bed, and  refuse
composition.

FINDINGS:   By  heating to 1,800 F, refuse or-
ganic matter is converted into  almost equal
weights  of a char (carbon),  combustible gas
and CO2, water, and  organic  liquids.  The
last is a complex mixture and  is suitable  as
a low-sulfur  fuel or chemical  raw material.
Sewage sludge, rubber,  and  plastics are rich
in combustible gases and liquids.
  The  yields depend on the rate of heating;
fast heating increases the yield  of  gas, while
slow heating increases that of char. The char
has  properties of activated carbon, and these
properties could be enhanced by further treat-
ment with steam, CO2, or air.
  The  organic liquids produced are  85 per-
cent of the  heavy  (viscous) oil variety;  15
percent is a  mixture  of methyl alcohol, acetic
acid,  butyric, and propionic acids, methyl-
ethylketone, furfural, and others. Acetic acid
is the major one of this group.
  The  gases  consist principally of COa, CO,
H2, CH4, C2H4, and  C2H6.  By removing the
COs,  a gas  of about 700  Btu scf is produced.
By  catalysis,  the gas  can be upgraded to ap-
proach 1,000 Btu pipeline gas.
  The gas  producer  has been built and pre-
liminary trials have been made, but test data
are not yet available. Experience and the pre-
liminary trials  indicate  that a hot, combust-
ible gas can be produced  continuously  by
burning refuse with a restricted air supply, if
the fusion (clinkering) of the ash  at the grate
can be controlled.
                 PUBLICATIONS

KAISER, E. R. Combustion  and heat calculations for in-
cinerators.  In  Proceedings; 1961 National  Incinerator
Conference, New York, May 18-20, 1964. American Society
of Mechanical Engineers, p. 81-89.
KAISER, E.  R.  Prospects for reducing  paniculate emis-
sions from large incinerators. Journal of the Air Pollution
Control Association, 16(6):324, June  1966. (Condensation.)

KAISER, E. R. A new incinerator control meter is needed.
In  Proceedings; 1966 National Incinerator  Conference,
New York, May 1-4, 1966. American Society of Mechanical
Engineers, p. 176-182.
KAISER, E. R. Chemical analyses of refuse components. In
Proceedings; 1966 National Incinerator Conference, New
York, May  1-4, 1966.  American Society of  Mechanical
Engineers, p. 84-88.

KAISER, E.  R., and  S. B. FRIEDMAN. The  pyrolysis of
refuse components. Combustion, 39 (ll):31-36, May 1968.

KAISER, E. R. Refuse reduction processes. In Proceedings;
the Surgeon General's Conference on Solid  Waste Man-
agement for Metropolitan Washington, July 19-20, 1967.
Public Health Service Publication No. 1729. Washington,
U.S. Government Printing Office, p. 93-104.

KAISER, E.   R. Successful  incinerators are  not  cheap.
Power,  113(9):78-79, Sept. 1969.

KAISER, E.  R.  The mounting  problem of solid wastes.
Power,  113 (10).-62-63, Oct. 1969.
 68

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                          Pyrolysis  of  Solid  Municipal  Wastes
                    Mr. Donald A. Hoffman
                       Utilities Department
                          City of San Diego
              San Diego, California  92101
 Grant No. EC 00266-04
 Funds Awarded: $96,280
 Project Period: June 1,  1965 to May 31, 1970
OBJECTIVES:  To  investigate  the  feasibility
of pyrolysis as an economic method of decreas-
ing the volume of solid municipal wastes and
of producing useful byproducts. To  deter-
mine the effect of temperature,  initial mois-
ture content, and various  types of refuse  on
the production of pyrolysis gases, liquids, and
solids.

APPROACH:  4-in.-diameter pyrolytic converter
was  constructed and fitted with appropriate
temperature and  pressure monitors and load-
ing and sampling openings. Several categories
of refuse—paper, leaves, wood,  glass, metals,
etc.—were pyrolyzed separately  and together
to determine the effect of temperature, pres-
sure,  and waste  composition on the  produc-
tion of gases, liquids,  and solids. The Btu
yield of  the various pyrolytic  products was
determined at the different temperatures and
pressures. The chemical composition of the
various products was also determined.
  After the performance of the 4-in.-diameter
pyrolytic converter had been evaluated, larger
converters,  as much as 18-in.  in diameter,
were  constructed and evaluated. In addition
to the effects of temperature, pressure, and
refuse composition, the effects of bulk density
of the refuse and residence time in the py-
rolyzer on the production of  the various py-
rolytic products were determined.

FINDINGS:  Pyrolysis is technically feasible as
a method of processing solid municipal wastes.
The energy content  of the products of pyrol-
ysis—the char and the "crude  vapor" (non-
condensable gases, tars, and liquid organics)
—is more than sufficient to sustain the process
once  it has been raised to the  selected tem-
perature.  In equipment  having  the  proper
overall thermal efliciency, the process may be
sustained by the  combustion of  the  "crude
vapor" only. The sulfur  content  in  the  tars
of this  vapor indicates that combustion of
this vapor to sustain the process  would give
stack emissions well within Rule 53(a) of the
San Diego County Air Pollution Control  Dis-
trict governing such emissions (0.2 percent by
volume as SO2). The optimum temperature of
pyrolysis with the minimum pyrolyzing time
occurs at  1,500 F with material having a bulk
density  of around  15  to 20 Ib/cu ft in  both
a 4-in.-diameter and  18-in.-diameter retort.
  The liquid fraction from pyrolysis is  suf-
ficiently  complex to  warrant a detailed  and
extensive  investigation.  Although  the   esti-
mated retail market dollar value of the liquid
organic compounds in this fraction is impres-
sive, it may well be that the cost of processing
and  separating  this fraction  to prepare the
organic compounds for marketing would be
so great as to  render  them noncompetitive.
  The carbonaceous  residue from the pyrol-
ysis  of  municipal-waste combustibles repre-
sents a  rich and reasonably easily transport-
able source of energy. The Btu yield of the
carbonaceous  residue from  the pyrolysis of
1 to  1.25 tons  of "typical San Diego  com-
bustibles" is equivalent to that of  1 barrel
(42 gal)  of Bunker "C"  fuel oil.  Moreover,
the  carbonaceous  residue,  when  properly
handled  and activated, provides  a material
whose  adsorptive  potential  is  equal or  su-
perior to  some  activated  carbons now  mar-
keted commercially.
  Most plastic materials  when pyrolyzed at
1,500 F depolymerize the carbon (plus inert
fillers) and gas and thus present no operating
problems.  Glass  softens during pyrolysis at
1,500 F but not to the extent that it  becomes
fluid. Thus glass should not present an oper-
ating problem. Iron and  steel are unaffected
by pyrolysis except that  the solders  used in
fabrication of some cans  melt and run. The
                                                                                       69

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quantity of metals  so  affected is  so  small as
not to cause operating problems. Aluminum
cans at 1,500 F behave  much the same as glass.
  Use of pyrolysis by  any community whose
solid waste classification approximates that of
San  Diego (i.e.,  by volume, 26 percent non-
combustibles  and 74  percent combustibles)
would result in a significant reduction in the
sanitary  landfill  space used  annually. This
potential annual reduction  could  reach as
high  as 70 percent,  depending upon  the char-
acter of the community's noncombustibles  and
the disposition of the  char.
  Pyrolysis of solid municipal wastes is a new
and unique approach to this problem, but no
capital and operating costs are available. It is
estimated, however, that the overall  unit  cost
of waste processing by pyrolysis  would  not
exceed   that encountered with  incineration
and  could possibly be lower.  Until such a
time as  an adequately sized pyrolysis unit is
constructed and  operated, the economic feasi-
bility of  this prdcess when  applied to solid
municipal wastes  will  remain a  matter  of
conjecture.


                PUBLICATIONS

HOFFMAN, D. A. Burns refuse  without  a flame.  The
American City, 82 (2): 102-104, Feb. 1967.

HOFFMAN, D. A.  Pyrolysis of solid municipal wastes. Sum-
marized in Engineering Foundation Research Conference,
Solid Waste Research and Development, University School,
Milwaukee, July 24-28,  1967. Conference  Preprint No.
F_l. 2 p.

JERMAN, R. I., and L. R. CARPENTER. Gas chromotographic
analysis of  gaseous products  from the pyrolysis of  solid
municipal waste. Journal of Gas  Chromatography,  6(5):
298-301, May 1968.

HOFFMAN, D. A., and R. A. FITZ. Batch retort pyrolysis of
solid municipal  wastes. Environmental Science and Tech-
nology, 2(11):1023-1026, Nov. 1968.

HOFFMAN, D. A. Processing of solid municipal wastes  by
pyrolysis. ASME. Paper No. 69-WA/PID-10. Presented at
Winter Annual Meeting, American Society  of Mechanical
Engineers, Los Angeles, Nov. 16-20, 1969. 8 p.
                      Citric Acid from Citrus Wastes by Fermentation
                         Dr. Sterling K. Long
        Citrus Agricultural Experiment  Station
                         University of  Florida
                 Lake Alfred, Florida   33850
  Grant No. EC  00258-03
  Funds Awarded: $43,803
  Project Period: Jan. 1, 1967  to Dec. 31, 1969
 OBJECTIVES:   To develop a procedure for con-
 verting the waste products of citrus-processing
 plants  and citrus molasses into useful prod-
 ucts, such as citric acid.

 APPROACH:   Selected  canning  plant  waste
 waters  having a high biochemical oxygen  de-
 mand (BOD) content were used to dilute citrus
 molasses to the optimum sugar concentration
 for  citric  acid  fermentation. Tapwater was
 used for the  dilutions in preliminary studies.
 The latter  determined  the conditions  and
 additives required to make the substrate suit-
 able for  the production  of citric acid  by
 strains of  Aspergillus niger.
   Three  different sizes  of  fermenters  were
 used for these studies. Fernbach Shake Flasks
 (0.3 liter) were used  to  determine the opti-
 mum  concentration of molasses, the possible
 effects of  interfering ions, and  the optimum
 environmental conditions for citric acid pro-
 duction  in  shake cultures.  In a 13.5-liter
 fermenter, the  effects of  aeration,  stirring,
 pH, and  temperature were studied. For  the
 final phases, results from the first two studies
 were  scaled up for pilot plant experiments
 with a 100-liter fermenter.

 FINDINGS:   Aspergillus niger NRRL 567 was
 used for the shake flask  and  pilot fermenta-
 tion  studies.  Efforts are  continuing  toward
 obtaining cultures with higher and more spe-
 cific acid  production capabilities.
   Stock inoculum cultures of A. niger NRRL
 70

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567 are maintained bn Potato Dextrose Agar
Slants. Inoculum culture is built up by trans-
fer to shake flasks  containing 10° Brix citrus
molasses.  The flasks are shaken for 3 days at
150 rpm,  28 C. An additional transfer is per-
formed under the  same conditions.  The final
inoculum is used at 3 to 5 percent of the total
substrate volume in the pilot fermenter.
   The  most  satisfactory medium  was  deter-
mined  to  be citrus molasses diluted  to  20°
Brix (approximately 9.5  percent total  sugars)
to  which  is  added  1.65  percent   (w/v)
K.4Fe(CN)6.  Anti-foam  is  added to  prevent
foaming during sterilization. The total  pilot
plant volume is 100 liters. Sterilization is ob-
tained at 121 C for 1 hr.
   The  best pilot  fermentation results  have
been obtained by allowing growth to develop
for the  first 18 to 24 hr with stirring at 150 to
200 rpm, but without sparging air.  The op-
timum  temperature is  28 C and  the pH is
maintained at 4.5. After  the initial growth
period, sterilized air  sparging at 0.5 scfm is
employed for 24 hr at the same stirring rate.
At  the 48-hr point, aeration is  increased to
1.0 scfm. Foaming is controlled by automatic
anti-foam addition. Total fermentation varies
from 76 to 86 hr and is dependent upon aera-
tion and  stirring rates.
    The maximum citric acid yield  obtained
so far was 58 percent of theoretical and aver-
ages at 49  percent.  Citric, succinic, and malic
acids are  the primary  acidic  fractions ob-
tained in the fermented beer. These acids are
generally obtained in ratios of 3  parts  citric:
2 parts succinic:  1 part malic. Work is con-
tinuing to  maximize citric  acid  production.
                     Garbage and Wastes for Mushroom Production
                        Dr. Seymour  S. Block
         Department of Chemical Engineering
                        University of  Florida
                 Gainesville,   Florida  32601
OBJECTIVES:  To investigate the production
of compost material from municipal and  in-
dustrial wastes capable of yielding mushrooms
for human consumption  and producing pro-
tein- and vitamin-rich fungus mycelia for ani-
mal feed and humus fertilizer.

FINDINGS:   When properly blended, fortified,
and composted, municipal and selected indus-
trial solid waste materials will support mush-
room growth and produce mushrooms in  good
yield and flavor. Analysis  of  the  spent resi-
due, composed  largely of mushroom mycelia,
showed it to contain more than  15 percent
nitrogen. The residue was shown to have po-
tential  as  a  feed  ingredient for  ruminant
animals. The following publications contain
detailed  results  gained  from  this research
project.

                PUBLICATIONS

BLOCK, S. S. Developments in  the production of  mush-
room mycelium in submerged liquid culture. Journal of
  Grant No. EF 00085-05
  Funds Awarded: $79,740
  Project Period: Jan. 1, 1959 to Dec. 31,  1964
Biochemical  and  Microbiological  Technology and Engi-
neering, 2(3):243,  Sept. 1960.

RAO, S. N., and S. S. BLOCK. Experiments in small-scale
composting.  Developments  in  Industrial  Microbiology,
3:326, 1962.

BLOCK, S. S., and  S. N. RAO. Sawdust compost for mush-
room growing. Mushrom  Science, 53:14,  1962.

BLOCK, S.  S. Effect of casing soils on the shape of the
mushrooms. Mushroom Science, 5:321, 1962.

AMMERMAN,  C. B., and S. S. BLOCK. Feed from wastes:
feeding value of  rations containing  sewage sludge  and
oakwood  sawdust. Journal of Agricultural  and Food
Chemistry, 12(6):539, Nov.-Dec.  1964.

BLOCK, S.  S. Composting conversion  of  solid wastes for
mushroom  growing.  Biotechnology  and Bioengineering,
6(4):403, Dec. 1964.

BLOCK, S. S. Garbage composting for mushroom produc-
tion. Applied Microbiology, 13(1):5, Jan. 1965.

BLOCK, S. S., and S. N. RAO. Small-scale composting for
mushroom growing  studies. Developments in  Industrial
Microbiology, 6:284, 1965.
                                                                                            71

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                      Partial Oxidation of Solid Organic Wastes
                    Dr. William W. Shuster
      Bio-Environmental Engineering Division
             Rensselaer Polytechnic Institute
                    Troy, New York   12181
OBJECTIVES:  To investigate the possibility of
converting organic solid  refuse and sludges
into useful products through a mechanism of
partial combustion using  limited  quantities
of oxygen in a fluidized bed.


APPROACH:   Major components of domestic
waste,  such as  paper and leaves,  as well as
dried sewage sludge, were studied  as sources
of  useful  products.  These  materials were
finely divided and supported in an air-nitro-
gen  stream containing less oxygen than re-
quired  for complete  combustion.  Reaction
was  carried out in a vertical tubular reactor
heated electrically.
  Gaseous products of reaction evolved from
the reactor were condensed and collected in
a series of traps held  at  progressively  lower
temperatures. Analytical methods applied and
utilized in the examination and identification
of major components in the complex mixtures
included wet chemical  methods, gas chroma-
tography  used  in conjunction with peak at-
 Grant No. EC 00263-03
 Funds Awarded: $63,510
 Project Period: May 1, 1966 to Apr. 30,  1969
tenuation and  a  syringe reaction technique,
infrared  spectroscopy, and mass spectroscopy.

FINDINGS:  Runs were  made in a  tempera-
ture range of 250 C to  1,000 C and with air-
nitrogen mixtures ranging from zero to 100
percent air. Products obtained and identified
included water, acetic acid, formic  acid, for-
maldehyde, methanol, acetone,  toluene, acet-
aldehyde, methyl acetate, ethyl vinyl  ether,
methane, carbon dioxide, carbon monoxide,
propylene,  ethylene, ammonia, ammonium
carbonate, and hydrogen.  In  general, runs
with  high  air-nitrogen  ratios  favored the
formation  of more  highly oxygenated com-
pounds,  while  a low air-nitrogen  ratio pro-
moted the formation of hydrocarbons.

               PUBLICATIONS

SHUSTER,  W. W.  Partial  combustion  of solid  organic
wastes. Presented  at Engineering Foundation Research
Conference, Solid Waste Research and Development,  II,
Beaver Dam, Wis., July 22-26, 1968. Conference Preprint
No. C_4.
                 Useful Disposal of  Auto  Bodies and Discarded Tires
                         Mr.  Eddie J. Wren
       Department of Environmental Sciences
               Gulf South Research Institute
             Baton Rouge, Louisiana  70808
 Grant No. EC  00275-01
 Funds Awarded: $44,374
 Project Period: Mar.  1, 1968 to Dec. 31, 1969
OBJECTIVES:   To develop an effective method
of compacting auto bodies and discarded tires
into levee and foreshore protection materials
with an interlocking configuration and a shape
to permit optimum weight and cost per square
foot coverage ratios. To design a complete
facility to  compact the  discarded  autos  and
tires and to develop suitable methods of pre-
venting potential stream pollution resulting
from their use.

APPROACH:  A  study of  various  configura-
tions  of compacted bodies was conducted to
determine  which configurations provided the
 72

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maximum area of protection- per ton of auto
bodies and  tires. Dies were constructed and
incorporated into a portable  car crusher  to
determine  their  effectiveness  in producing
suitable  interlocking bales.  In  addition  to
compacting  the auto bodies,  attempts  were
made to incorporate discarded  tires  in the
bales. The effect of heating the tires before
incorporation into the  bales was studied  to
determine if the  softened tires help hold the
bales together  and provide some protection
against stream  pollution by partially coating
the metal.  Finally, the  economics of  a  com-
plete compacting operation was developed.

FINDINGS:  The conclusions reached as  a re-
sult of this study are as follows:
   1. The use of compacted automobile bodies
for large-scale Mississippi River levee  protec-
tion is not economically feasible or  practical,
because  of  the vast  quantities  required  in
contrast  to  the relatively small tonnage  of
available  automobile  bodies  within reason-
able hauling distances.
  2. The density of compacted automobile
bodies (even with asphalt sand mixes added)
is much too small (light) to replace the  much
denser riprap (broken stone) presently  being
used for construction  work in the relatively
high-velocity currents of the Mississippi River.
  3. Compacted automobile  bodies can  be
economically  used (disposed  of)  in certain
small-scale applications such as the hypothet-
ical marshland shoreline erosion control work.
  4. An observation based on the research
team's association with  this  work  indicates
that some form of bounty or  subsidy should
be provided in the original purchase price of
all  metal products (not just  automobiles)  to
assist in the economics of recycling all metals
to the  scrap processors in the  interest of con-
servation  of natural  resources.
                 Biological Conversion of Animal Wastes  to  Nutrients
                         Dr. Byron F. Miller
               Department of Poultry Science
                   Colorado State University
              Fort  Collins, Colorado   80521
  Grant No. EC 00262-02
  Funds Awarded: $41,634
  Project Period: June 1, 1968 to May 31, 1970
OBJECTIVES:  To investigate the digestion of
poultry manure  by flies and  establish hus-
bandry procedures for caring for fly larvae on
a manure medium.  To  measure changes ac-
complished  in  poultry  manure by these or-
ganisms, and  their  efficiency.  To determine
the value of the protein material as a feed-
stuff for poultry.

APPROACH:  Fresh  raw  poultry manure  was
"seeded" with fly eggs to convert the  manure
energy into useful  animal  protein.  Samples
of the  manure were  analyzed for composition
and nutritive value before and  after digestion
with  fly  larvae. Environmental  conditions
such as temperature, moisture  content of the
manure,  humidity,  and  ratio of eggs to  ma-
nure  conducive  to  optimum  conversion of
the manure  to  pupal protein were  studied.
The protein  material was analyzed for nutri-
tive content,  metabolizable  energy, and abil-
ity to support growth in young chickens.

FINDINGS:  Five  species  of  Diptera  (flies)
were screened as potential means of  convert-
ing poultry manure  to high-quality protein
for animal feed. Musca domestica (housefly)
was selected  because it reproduced  in large
numbers and required a minimum  of time
(5 to 10 days) to reach pupal  stage. It was
found  that 3 g  (about 60,000) of fly eggs to
4 kg of manure gave optimum yield of pupae.
The fly  larvae effectively reduced the prob-
lem of manure disposal by eliminating 60 per-
cent of the moisture and 80 percent of the
organic matter during  the  digestion  period.
                                                                                       73

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In addition,  the wet,  pasty, odoriferous ma-
nure was  converted to a granular, stabilized,
inoffensive product that was easily dried.
  About  2 percent of fresh manure weight
was harvested as dried fly pupae. These pupae
continued 60 percent  protein,  comparable to
fish meal  as a protein supplement for starting
chickens.  The pupae are a good source of
minerals and of some  vitamins.
  Since the  housefly feeds on  a wide variety
of waste materials it may prove useful in solv-
ing other waste disposal  problems. Through
the controlled production  of  fly  pupae, the
number  of wild flies  would be reduced be-
cause  their  breeding  sites are  eliminated.
While helping to solve a very difficult waste
problem the  housefly can  be used  as a protein
supplement  and aid in  the control  of wild,
disease-carrying flies.  Most  of the  fertilizer
value is retained in the manure residue.
  A poultry operation of 40,000  laying hens
would produce 1,600 Ib  of dried fly pupae
daily.  At a  price of 10 cents/lb, this would
amount to $160/day. In addition, the manure
residue could be  used as fertilizer.
  Feeding trials with growing broiler stock
indicated that pupal protein  can be used
readily as the primary protein supplement in
broiler diets. Pupae were used to replace  soy
bean oil meal, fish meal, meat and bone scraps,
trace  minerals, and  B vitamin  supplements
in a standard broiler diet. The control diet
resulted in slightly greater body weight, which
was not,  however, significant at the 5  percent
level. The  pupae  diet resulted in  slightly
better feed efficiency,  which  again was  not
significantly  different. Normally  fly  pupae
would be included in poultry diets at about
5 percent  of  the diet  instead of 30  percent
as used  in  this  study.  The  metabolizable
energy of  the pupae was found to be 1,149
cal/lb.
                PUBLICATIONS
 MILLER, B. F., and J. H. SHAW.  Digestion of  poultry
 manure by  diptera.  Poultry  Science,  48 (5): 1844-1845,
 Sept. 1969. (Abstract.)

 MILLER, B. F, Biological digestion of manure by  diptera.
 Feedstuffs, 41(51):32, Dec. 1969. Presented at Pacific South-
 west Animal Industry Conference, Fresno, Nov. 17, 1969.
 Sacramento, California  Grain and Feed Association.
                              Biological  Methane Formation
                        Dr. Marvin P. Bryant
                 Department of Dairy Science
                        University of  Illinois
                     Urbana, Illinois  61803
  Grant No. EC 00289-04
  Funds Awarded: $169,517
  Project Period: June 1,  1966 to May 31, 1970
 OBJECTIVES:   To obtain  fundamental  eco-
 logic,  nutritional, and biochemical  informa-
 tion applicable to a general  understanding of
 the  process  of methane  formation  from or-
 ganic  matter in natural systems. Special em-
 phasis was given to those habitats, e.g., sewage
 sludge digesters and  the digestive  tracts  of
 ruminants, in which anaerobic decomposition
 of organic wastes leads to methane formation.

 APPROACH:  Characterization of isolated meth-
 ane  bacteria included nutritional studies  to
 establish  the relationship of the nutrient re-
 quirements of the organism to the chemical
 composition of the natural  habitat. The bio-
 chemistry of methane  formation was studied
 in the Methanobacillus omelianskii, as well as
 in other methane bacteria of quantitative sig-
 nificance in natural environments, in order
 to compare the  mechanism of methane pro-
 duction in  various bacteria  that produce
 methane from  organic substrates,  hydrogen,
 and carbon dioxide.  Other aspects of the bio-
 chemistry of methane  bacteria, e.g., electron
 transport systems and biosynthesis of cell con-
 stituents, were also studied.
 74

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FINDINGS:   Our work'has resulted  in  great
modification of theory about the bacteria con-
cerned and intermediary metabolism involved
in degradation of organic wastes by methane
fermentation.  Earlier studies indicated  that
methane-forming bacteria produced methane
by degradation of acids, alcohol, and hydrogen
produced  from  organic wastes by  nonmeth-
anogenic bacteria. We showed, however, that
ethyl  alcohol is not fermented by the meth-
anogenic species Methanobacillus omelianskii.
This  species was shown  to  be  a  symbiotic
association of  two  species.  One species  is
nonmethanogenic and produces acetate and
hydrogen  from alcohol but cannot  carry this
out as a pure culture because the  hydrogen
produced  inhibits its growth. The other spe-
cies utilizes hydrogen produced by the first
species to  obtain energy for growth via reduc-
tion of carbon dioxide to methane. The main-
tenance of the low  partial pressure of hydro-
gen allows  the alcohol-degrading species  to
grow. Several species of  bacteria have been
shown to oxidize alcohols and lactic acid when
grown in association with the hydrogen-utiliz-
ing methane bacteria. The work indicates that
similar  symbiotic associations of  hydrogen-
utilizing methane bacteria with nonmethano-
genic species is probably responsible for deg-
radation of fatty acids  other than formate
and acetate, and emphasizes the importance
of  methane  bacteria, serving  as  hydrogen
sinks, in  allowing  other  bacteria to oxidize
organic wastes more efficiently.
  Studies  have confirmed  other  recent work
indicating that the hydrogen- carbon dioxide-
and   formate-utilizing  species  Methanobac-
terium ruminantium and M. formicicum are
among the most numerous methane-forming
species in sludge. Two  new  species utilizing
these  energy sources have been isolated. These
studies  demonstrated the  great  diversity  of
species of  methane bacteria that utilize hydro-
gen-carbon dioxide and formate.
  Studies  on  nutrients essential or stimula-
tory to growth  of  two of the  more impor-
tant hydrogen-utilizing methanogenic species
showed  the  great importance of acetate as a
major carbon  source, ammonia as the major
nitrogen source, and sulfide as sulfur source.
These bacteria  are unable to utilize amino
acids  or peptides effectively either as carbon
or nitrogen sources. Some  strains require an
unidentified  growth factor  in  very  small
amounts. We  previously developed methods
for isolation of the factor from sewage sludge
or rumen contents but could  not obtain large
enough amounts of factor for definite charac-
terization.  We now find that it is  produced
by  other methanogenic  species in  amounts
that should make identification feasible. Es-
tablishment of nutrient requirements of meth-
ane  bacteria may give information of value
to development of methods  for  more rapid
anaerobic degradation of organic wastes.
  Methods were developed, for the  first time,
for pure, large-scale cultures of methanogenic
bacteria in culture  media  with  hydrogen-
carbon dioxide as energy source.  This  has
made it possible  to study effectively the bio-
chemistry of these bacteria.
  Knowledge  of  biochemical mechanisms by
which a hydrogen-utilizing methane  bacterium
reduces carbon dioxide to  methane has been
increased.  It  has  been shown that ATP  in
catalytic amounts and a low-molecular-weight,
unidentified methyl  carrier,  present  in ex-
tracts, are  essential for methane  formation
from either carbon dioxide or methyl  cobala-
min. Studies on identity  of the methyl carrier
are in progress. The bacterivun contains large
amounts of a  compound involved in electron
transport that is fluorescent and dialyzable in
the  oxidized state but is bound  to the  non-
dialyzable  fraction of the  extract and is not
fluorescent  when  extracts  are reduced by
hydrogen.  The compound  has been isolated,
and studies on its identity and  function  in
electron transport are  underway.  The cell
extracts produce  methane  from the one car-
bon of pyruvate, the three carbon  of serine,
and from  the one-carbon  derivatives  of N10
formyl-, N5, N10-methenyl-, N5, N10-methylene-,
and N5 methyl-tetrahydrofolate,  and from
methylcobalamin, but it is  not yet  known
whether these compounds  are  significant in-
termediates in reduction  of carbon dioxide to
methane.

               PUBLICATIONS

BRYANT, M. P., E. A. WOLIN,  M. J. WOLIN, and  R. S.
WOLFE. Methanobacillus omelianskii, a symbiotic associa-
tion of two species of  bacteria. Archiv fuer Mikrobiologie,
59(l-3):20-31, Aug. 1967.
                                                                                      75

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BRYANT,  M. P.,  B.  C.  MCBRIDE,  and  R. S.  WOLFE.
Hydrogen-oxidizing methane bacteria. I. Cultivation and
methanogenesis. Journal of Bacteriology, 95(3)1118-1123,
Mar. 1968.

LANGENBERC, K.  F.,  M. P. BRYANT, and  R. S. WOLFE.
Hydrogen-oxidizing methane bacteria. II. Electron micros-
copy. Journal of Bacteriology, 95(3):1124-1129, Mar. 1968.

MCBRIDE, B. C., J. M. WOOD,  J. W. SIDERT, and B. N.
SCHRAUZER.  Methylcobalt derivatives of  vitamin  Bs,12s,
model compounds as substrates  in enzymatic methane
formation.  Journal of the American  Chemical Society,
90(19):5276-5277, Sept. 11,  1968.

WOOD, J. M., F.  S., KENNEDY, and C. G. ROSEN. Synthesis
of methyl-mercury compounds by extracts of a  methano-
genic bacterium. Nature, 220:173-174,  Oct. 12,  1968.
ROBERTON, A. M.,  and R. S'. WOLFE.  ATP  requirement
for methanogenesis in cell extracts of  Methanobacterium
strain  M.  O.  H. Biochimica et  Biophysica Ada, 192(3):
420-429, Dec. 30, 1969.

ROBERTON, A. M.,  and R. S. WOLFE. Adenosine triphos-
phate pools in Methanobacterium. Journal of Bacteriology,
102(1):43-51, Apr. 1970.

KENNEDY, F. S., T.  BUCKMAN, and J. M. WOOD. Carbenoid
intermediates  from the photolysis of haloalkylcobalamins.
Biochimica et  Biophysica Ada,  177(3):661-663, May 6,
1969.

WOOD, J.  M. Environmental pollution by  mercury.  In
R. R, Metcalf, and J.  Pitts, eds. Advances in environ-
mental science, v. 2. New York,  John  Wiley 8c Sons,  Inc.
(In press.)
                        Chemical  Transformation  of Solid  Wastes
                          Dr.  Virgil H.  Freed
         Department of Agricultural Chemistry
                      Oregon State University
                    Corvallis, Oregon   97331
  Grant No. EC 00242-04
  Funds Awarded: $136,562
  Project Period: Oct. 1, 1966 to Sept. 30, 1971
OBJECTIVES:   To  classify  and  identify  the
chemical constituents of municipal and agri-
cultural field solid wastes, to investigate meth-
ods of chemical transformation of these solid
wastes  to products  of useful  value, and to
follow the development of suitable laboratory
procedures  with  additional  studies at  the
pilot-plant scale.

APPROACH:   Initially,  the chemical  composi-
tion of the various portions of solid waste was
determined. Efforts were then directed  to the
chemical  transformation  of  the  components
of various wastes into useful products.  Re-
actions   being  studied   for  the   chemical
transformation  of cellulose include  catalytic
destructive  distillation, high-pressure  hydro-
genation,  and ether and ester formation. Ex-
periments involving ether and ester formation
are being  conducted to unite  nitrogen  and
phosphorus chemically to the cellulosic struc-
ture and, thus,  to form a usable soil additive
from the  cellulose.  In  another  series  of ex-
periments, cellulose  is being extracted  from
waste  materials by  xanthate formation  and
the extract evaluated  as  a  raw  material for
the commercial production of plastics.
   The  chemical   transformation  of  plastic
wastes  to  usable products  through high-pres-
sure hydrogenation, oxidation, destructive dis-
tillation, and extraction is  being investigated.
Metal  extraction  procedures  are  also  being
investigated  to determine  the feasibility  of
recovering various  metals  either  as salts  or
in a  pure state from solid waste.
   The last  phase  of this  study involves the
application of useful transformation reactions
to the  solution of  solid waste problems on a
larger  scale. The  most promising  chemical
transformation reactions being studied in the
laboratory will lead to studies of pilot-plant
operation and  associated  engineering  prob-
lems, and to an evaluation of economic factors.

FINDINGS:   Information  about the  chemical
composition  of most  wastes  is available  in
the literature.  Municipal refuse, straw, bark,
wood, and paper contain high percentages  of
cellulose.
   Destructive  distillation  and high-pressure
hydrogenation of  organic   wastes  produce a
combustible gas, a heterogeneous liquid, and
a  carbon/ash  solid residue. The liquid pro-
duced by hydrogenation of bark, for example,
76

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contains  about 65  percent  aromatic  com-
pounds and 35 percent aliphatic compounds.
  The use of a catalyst or chemical  reactant
during destructive distillation affects the com-
position of the products.
  The formation of cellulose esters and ethers
from  waste  cellulose  is a practical means of
producing usable  products. The cellulose in
paper  or straw can  be acetylated  by one of
three processes (solution, fiber, or vapor) to
produce cellulose acetate, which can be formed
into a solid  sheet under pressure and elevated
temperature. Such a  solid sheet should have
applications as a construction  material, lami-
nate, container, and so forth.
  Purified  cellulose  from wastes can be used
as the raw material for the  production of
derivatives  such as cellulose  nitrate, methyl
cellulose, and cellulose butyrate.
  The cellulose of a complex waste  such as
municipal refuse can be partially purified by
acid washing  to remove the available metals
and salts. Glass, rocks, and other dense mate-
rials can be separated by settling in a liquid
medium. The metal content of straw can also
be  reduced by acid washing.
  Straw  pulp  (cellulose)  can be  purified by
using any of several techniques, including the
nitric acid-pulping  process   and  the  soda
process.
  Waxes, fats, and oils can be removed from
solid wastes by solvent extraction.
  Cellulose xanthate can be formed from the
cellulosic component of solid wastes. This
compound  is  soluble in sodium  hydroxide.
Cellulose  can be precipitated upon neutrali-
zation  or derivatives such  as zinc xanthate
can be produced.
  Phosphoric acid  and urea  can  be used to
form cellulose derivatives that are  water  in-
soluble.  The  ammonium  salt of cellulose
phosphate, or the amide, contains two plant
nutrients  that are not leached out  by water.
A greenhouse soil  test  indicates  that  this
material  is  effective  in  stimulating  plant
growth  when applied in the same nitrogen
concentration as a commercial fertilizer.
  The nitrogen content  of cellulose can be
increased by up to  12  percent by reaction
with urea through  the formation  of cellulose
carbamate.
  The wide range of plastics being used today
makes a  single chemical   treatment process
most  unlikely;  however, some  plastic mate-
rials can be dissolved in organic solvents and
others can be degraded by  acid or base treat-
ment.  Hydrogenation of plastics is a promis-
ing potential means of converting plastics to
oil, but the  appropriate  reaction conditions
and catalysts have not yet been defined.
  The  most promising  chemical  treatment
processes  for further study appear  to be  the
use of waste cellulose by ester and ether for-
mation,  the  hydrogenation of wastes to  oil,
and the nitrogen and phosphorus enrichment
of wastes. Plans for economic evaluation and
larger scale studies are underway.
  Some  industrial interest in  waste  utiliza-
tion has been received, especially for cellulose
utilization and plastic production.
                   Converting Incinerator Residue  to  Useful Materials
                     Dr. Peter E. D.  Morgan
       Department of Materials  Science and
                                Engineering
       Franklin Institute Research  Laboratories
          Philadelphia, Pennsylvania   19103
  Grant No. EC 00326-01
  Funds Awarded: $50,734
  Project Period: May 1, 1969 to Apr. 30, 1971
 OBJECTIVES:   To investigate  the  possibility
 of  developing a process for the direct  con-
 version  of  incinerator residue by  calcining,
 melting,  and slagging to a dense  aggregate
 useful for road building or road surfacing or
 as a filler material for concrete. Because most
 municipalities are involved both in waste  dis-
 posal and  in road-building programs, a direct
                                                                                        77

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path to recycling and  effective utilization of
this waste product is envisioned.

APPROACH:  A laboratory experimental eval-
uation of the  thermochemistry of processes
designed either to melt down,  slag,  or  con-
solidate incinerated waste residues has been
undertaken. From  this investigation, param-
eters  are  emerging to permit recommenda-
tions  for optimum burning and calcining
conditions for waste products.
  After  the laboratory  studies, preliminary
design and cost estimates for a system to per-
form  the needed  thermochemical  operation
were made.  A small pilot plant has been de-
signed and constructed to handle a sidestream
of ash from an existing municipal incinerator
so that the final design criteria and economics
for a  full-scale  plant can be developed.

FINDINGS:  Philadelphia incinerator  ash  has
been  ground, fired, and milled to produce  a
ceramic  oxide  powder.  An  analysis  for  im-
portant elemental content has been made; it
has been shown that this powder has  thermal
properties expected for the analyzed composi-
tion in terms of sinterability, fluxing behavior,
etc., both alone and  with  additives. It  has
been  possible, by  these studies, to produce  a
very high-grade ceramic material  that might
be used for bricks or  as a facing material.
  For example, nonporous samples have been
made with densities reproducibly at 2.90 g/cc
and tensile  strengths of 7,000 to  15,000  psi.
Crushing strength (not measured)  may be ex-
pected to be around at  least 50,000  psi, and
the material would fulfill any ordinary build-
ing requirements.  Little modification of  a
brickworks would be necessary for the adapta-
tion to a raw material of this type rather than
to the ordinarily used clays.
  Extensive  firings with  additions of lime
have demonstrated the  feasibility of turning
the solid waste ash into cement powder and
ultimately  into  some  form of  concrete. At
present it appears that a composition allow-
ing the formation of 2CaO.SiO2 and 2CaO.
Fe2O3 during firing at 1,350 C produces the best
cement  powder.  Further study is rapidly con-
tinuing in this  area.  More importantly,  the
incinerator waste cannot only form a concrete
mix but can also be used as an aggregate filler.
  Ash has been  given three different thermal
treatments to produce aggregates for possible
road  use in both concrete and bituminous
surfaces.
   Both the Pennsylvania and  Federal high-
way authorities have agreed to test aggregates
produced,  and  it  is  hoped  that  they  can
proceed eventually to  the actual laying of
stretches of  highway.  Preliminary tests  for
friability, abrasion resistance, and chemical re-
sistance are all encouraging. This area prom-
ises the most immediate  use  because cities
that produce the solid  wastes are also in the
business of road building and topping; there-
fore, problems of logistics and economics are
minimal, and this use  involves  probably the
fewest changes in present policies. It is hoped
that, later, the more  remote possibilities can
be  brought  to  fruition  once  at  least  one
scheme for usage is under way.

                PUBLICATIONS
New twist in waste use. Chemical Week, 106 (2):58, Jan.
14, 1970.
                        Degradation of Waste  Paper  to  Protein
                    Dr. David M.  Updegraff
                  Denver Research Institute
                      University of Denver
                  Denver,  Colorado  80210
 Grant No. EC-00271-02
 Funds Awarded: $165,160
 Project Period: June 1, 1967 to May 31,  1970
OBJECTIVES:   To  evaluate  a  fermentation
method of converting waste paper to a protein
supplement for livestock feed, the specific ob-
jective  being to  obtain  an  extremely fast-
78

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growing, cellulose-digesting organism  having
a high nutritional/protein value.

APPROACH:   The initial effort included isola-
tion and screening of microbes to find suit-
able strains for rapid digestion of cellulose in
a water medium enriched with hydrocarbons,
oxygen, and nitrogen. The work centered on
the isolation of hydrocarbon-utilizing, cellu-
lose-digesting organisms by employing enrich-
ment, sprinkle plate, percolation, and garden-
ing  isolation  techniques. These  organisms
were  purified and screened for growth. Cell
yield, hydrocarbon utilization, cellulose deg-
radation,  and amino  acid profiles were de-
termined.  The  next  phase  involved  the
optimization of the fermentation process with
a selected optimum growth organism. These
studies  investigated the following variables:
pH, temperature, aeration, CO2 requirements,
trace  elements, nitrogen sources, stimulators,
and the effects of certain fractions of waste
paper. A comparison of a batch versus a con-
tinuous fermentation  investigated the effects
of each on product quality and toxicity.

FINDINGS:  The  initial  phase  isolated  367
pure  cultures on  n-hexadecane media  from
more than 70 different inocula of soil,  com-
post,  sewage sludge,  and forest litter; 28 of
these were found  to  be capable of attacking
sodium carboxymethyl cellulose and lowering
its  viscosity.  Only one proved to  be capable
of  attacking  purified  cellulose,  ball-milled
newspaper,  or  newsprint. This culture is a
fungus  that grows well at up  to 45 C, identi-
fied as Aspergillus fumigatus. Unfortunately,
this organism is  a known pathogen,  and so
cultivation on a large scale is believed to be
not advisable.
  More  than  300 enrichment cultures  were
also developed on  cellulosic substrates  from
similar  inocula. These were tested in shake
flask fermentations for ability to produce pro-
tein and utilized  the aforementioned  sub-
strates.  Only 10 enrichment  cultures yielded
greater  than 0.2 mg  of protein per ml  in 5
days.  Five of these, all fungi, were studied
in  shake flask  fermenters  in  an effort  to
achieve optimum conditions  for protein syn-
thesis and cellulose utilization. The organisms
isolated,  Myrothecium  verrucaria,  Tricho-
derma viride, Aspergillus  fumigatus, and
Cellulomonas are from genera long known to
be actively cellulolytic.
  Myrothecium verrucaria  gave the highest
rates of protein synthesis of the fungi studied;
therefore,  scaled-up  studies  using 14-liter
stirred-jar fermenters concentrated on this or-
ganism.  Protein  yield  on  ball-milled  news-
paper increased with substrate concentration
up  to the  maximum used. A  very simple
medium  containing dibasic  ammonium phos-
phate, urea,  and yeast autolysate proved op
timal  for  protein  synthesis  and  cellulose
utilization. At a concentration  of  4 g ball-
milled newspaper per  100  ml  medium, the
maximum rate of cellulose  consumption was
5.4 g per liter per day and the rate of protein
synthesis was 0.3 g  per  liter  per day. The
maximum yield of protein obtained was 1.42
g/liter by a highly  specific modified Biuret
method,  or 3.3 g/liter by the usual method of
multiplying the total  organic (Kjeldahl) nitro-
gen  by 6.25.  The amount of cellulose con-
sumed under these conditions was 12.7 g/liter
from an  original 20.4  g/liter  contained  in
40 g/liter of ball-milled newspaper.
  Chemical analysis  of the dried final prod-
uct indicates  it may  be a nutritious animal
feed. The literature  does not  list  Myrothe-
cium verrucaria  among  the mycotoxin-pro-
ducing fungi;  however,  preliminary feeding
studies with mice and rats would  be  desir-
able before  proceeding with pilot-plant con-
struction in order to obtain some evaluation
of its toxicity and dietary value.
  The work  accomplished was nearly suffi-
cient to  permit the  design  and  construction
of a  pilot plant, although a few more stirred-
jar runs  using larger concentrations of ball-
milled paper and perhaps  larger  concentra-
tions of ammonium phosphate and  urea may
be desirable.
               PUBLICATIONS

UPDEGRAFF, D. M. Semimicro determination  of cellulose
in  biological  materials.  Analytical Biochemistry, 32:420-
424, 1969.
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                    Engineering Properties of Compacted Ash- Fills
                       Dr.  Donald H. Gray
            Department of Civil Engineering
                     University of Michigan
              Ann Arbor,  Michigan   48104
 Grant No. EC 00317-02
 Funds Awarded: $40,455
 Project Period: Mar. 1,  1969 to Feb. 28, 1971
OBJECTIVES:  To determine the physical and
engineering  properties of  both  compacted
fly  ash  and  incinerated sewage  sludge and
to determine any environmental or health haz-
ards associated with the use  of  these  mate-
rials for fill purposes.  Once  the properties
of the ash material are determined, decisions
about their use as fills to support heavy loads
can be  made,

APPROACH:   The  engineering properties  of
fly  ash  and  incinerated sewage   sludge  are
being determined. The index properties and
composition  of ashes are being  defined by
various  methods,  including  grain size dis-
tribution, specific gravity,  grain  shape, and
ignition  loss tests among others. The com-
paction  characteristics are determined by im-
pact compaction  and  kneading  compaction
tests.  Strength  properties  of  compacted fly
ash are  denned  by unconfined  compaction
tests,  CRB  tests,  triaxial compression  tests,
and ash-hardening tests. The  settlement and
compressibility behavior are  determined by
an  in situ measurement of  the coefficient of
compressibility of the ash fills by the  use of
a Dutch cone penetrometer. Frost susceptibil-
ity is determined by standard grain size analy-
sis and frost heave tests. The effect on strength
and frost susceptibility of low-level additions
of cement,  lime,  and asphalt is  also  being
determined.
  The  hazards associated with the  implace-
ment of ash fills are being investigated.  Anal-
ysis of the ash leachate reveals the pH, BOD,
COD, total  soluble salt content,  major ions,
and toxic compounds. The corrosiveness  of
the compacted ash is determined by its bulk
electrical  resistivity,  redox  potential,  and
weight  loss  coupon analysis. Ash fill aggres-
siveness toward vegetation and moisture reten-
tion characteristics are also being  determined.
FINDINGS:   The fly  ash under  investigation
was obtained from four coal-fired stations in
Michigan. The fly ashes were selected as rep-
resentative of the  typical range  of ashes pro-
duced  by coal-fired  power stations.  The
sewage sludge  ashes were obtained  from  10
treatment plants scattered all over the nation.
The sewage  sludge ashes were  likewise  se-
lected  to provide  a range  of  possible  ash
types.
  The fly ash study is focusing  primarily  on
the compressibility  and frost  susceptibility
of this material, because these  are  the two
properties about which least is known and
the ones  that  might  preclude  its use  as a
structural fill material in engineering prac-
tice. The sewage  sludge ash study,  on  the
other hand, is attempting to characterize  this
since there is no published information on it
at all.
  Index  property  tests  and chemical compo-
sition analyses  have  been completed  on both
types  of ashes. Both the sewage  ash  and the
fly ash are predominantly silt-size material.
  Strength-compaction  tests  have also been
completed on  all ashes in  addition to  age
hardening tests  and  lime-cement stabiliza-
tion tests. Strength  falls off markedly  for
samples  compacted wet of  optimum;   this
trend is  even  more  pronounced with com-
pacted fly ash.  Most ashes,  particularly  the
sewage ashes  with large free-lime contents,
exhibit as much as a twofold increase in un-
confined  compressive strength with time. The
addition  of  as  little as 3 percent cement  by
weight to nearly all the sewage  sludge ashes
is  sufficient  to  give  them  enough   strength
when compacted  to meet  easily minimum
strength  requirements  for subbases  in road
construction.
   When mixed with  the  right amount of
water  and  about  10   percent  cement   by
80

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weight  and  then  compacted  statically  to
about  5,000 psi,  some of  the  sewage  ashes
approach  the  strength of a lean concrete. As
a result we are preparing now to manufac-
ture some trial building  blocks  for  experi-
mental purposes from sludge ash supplied by
the Pontiac, Michigan, plant.
  A frost heave testing facility has been  de-
signed  and  constructed;  experiments   are
presently  under  way  on various  compacted
ashes. The  pH of all  the sewage  ashes  has
been measured and found  to be quite alka-
line  (pH 10 to 12). One of the sewage ashes
(from Pontiac, Michigan) is quite  corrosive
when it comes in contact with metal.
               PUBLICATIONS
GRAY, D H. Properties of a compacted sewage ash. Journal
of the  Soil Mechanics and Foundations Division, Ameri-
can  Society  of Civil Enginecis,  96 (SM2):439-451,  Mai.
1970.
                  High-Energy  Gas  from  Refuse  Using  Fluidized Beds
                       Dr. Richard C. Bailie
         Department of Chemical Engineering
                    West Virginia University
          Morgantown, West Virginia   26506
 Grant No. EC  00399-02
 Funds Awarded: $272,556
 Project Period: Jan. 1, 1969 to Dec. 31, 1970
OBJECTIVES:   To investigate several possibili-
ties  in  the operation of a  fluidized  bed  of
sand for the disposal of solid waste. Complete
combustion, incomplete oxidation, and pyrol-
ysis  are the three alternative processes availa-
ble  for  the  recovery of energy content  of
refuse in a fluidized bed.

APPROACH:   Cellulose  and  other polymeric
materials are contacted with  air, inert gas,
steam,  and combinations of these gases in a
fluidized bed. This  results in oxidation, pyrol-
ysis, and  anaerobic decomposition reactions.
For  each type  of  operation,  an attempt  is
made to recover evolved heat or organic com-
pounds,  or  both,  and gaseous hydrocarbons
in varying amounts. Maximizing the yields
of hydrogenated gas of high  heating value
is emphasized. Temperatures of  1,300, 1,500,
and  1,700 F  and pressures from atmospheric
to  100  psi  are used  together with  several
homogeneous   semifluid  feeds and  several
feed rates. Fluidization variables of particle
size  and  gas  velocity are investigated,  and
the  product  is  analyzed  for heating values
and  carbon-hydrogen  ratios.  Residues  are
analyzed for  ash, sand,  and unburned solids.
FINDINGS:  Investigations have shown that the
gaseous products resulting  from the thermal
decomposition  of  cellulosic  materials  are
sensitive both to the rate of heat transfer  to
the sample and to the  temperature of the
surroundings. At high heat transfer rates the
cellulose polymer  decomposed to hydrogen-
ated gases  and at low rates more oxygenated
gases  were formed. The fluidized bed results
in rapid heat transfer, and this leads to higher
yields  of hydrogenated materials. The quan-
titative values have not been  established.
  A mathematical  model  developed to de-
scribe  the pyrolysis  or  pyrolysis-combustion
of cellulosic material takes  the following fac-
tors into consideration:  (1) heat transfer by
conduction,  (2) heat transfer by radiation,
(3)  sample geometry, and  (4) bulk flow  of
pyrolysis out of sample.  The model is useful
in explaining many experimental observations
appearing  in literature as well as the unique
effects contributed  by the fluidized bed.
  Steady-state experiments  have been  per-
formed  on the  conversion of  an  aqueous
slurry  containing  20 percent solids  in the
fluidized bed.  These  solids were  mainly  1-
methylaminoanthraquinone  or other insolu-
                                                                                        81

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ble organic  dyes. Experimental parameters
were airflow  rate, bed height, and bed tem-
perature.  It  was observed that the  organic
dye compounds readily underwent pyrolytic
decomposition  owing to the  high  heat trans-
fer rates present. At temperatures of  1,600 F
oxidation followed within the bed in a smooth
manner.  At lower temperatures a noticeable
fraction  of   the  decomposition  products
emerged from the bed, especially at  low air
rates. This latter material underwent oxida-
tion in the free-board space or was elutriated.
                    Kinetics  of Porteous  Refuse  Hydrolysis  Process
                      Dr.  Hans E. Grethlein
               Thayer School of Engineering
                         Dartmouth College
           Hanover, New Hampshire  03755
  Grant No. EC 00279-02
  Funds Awarded: $70,348
  Project Period: June 1, 1968 to May 31, 1970
OBJECTIVES:   To determine the reaction kine-
tics for the formation of glucose from cellu-
lose-containing  materials  found  in  solid
wastes, and the subsequent decomposition of
the glucose in a high-temperature, low-acid-
concentration hydrolysis process. To conduct
a process design and economic evaluation of
the hydrolysis process  for  the fermentation
production  of ethanol  from cellulose found
in solid wastes.
APPROACH:   The rate at which glucose forms
and decomposes at various temperatures and
acid concentrations was  determined  experi-
mentally in a small batch reactor. Once the
reaction rates were known,  the  time to  opti-
mum glucose yield could be calculated by
using the  relationship for  consecutive  first-
order reactions. Next a  reaction vessel was
designed and constructed to  permit the sepa-
rate heating  of a cellulose slurry and an acid
solution. Once the desired reaction tempera-
ture was obtained, the reagents flowed through
a  mixing tee and  a  reaction chamber.  The
reaction was  then  quenched, and the amount
of glucose  produced was  determined to con-
firm the reaction rates found in batch opera-
tion. Once  reaction  rates  were  accurately
known, a  full-size hydrolysis plant was de-
signed and an economic evaluation performed
to determine the cost  of  producing glucose
for a fermentation process.

FINDINGS:  The  acid hydrolysis of cellulose
in paper follows a sequential, first-order, kine-
                             ki         k2
tic model, namely, cellulose —> sugar —>
decomposed  sugars.  The  rate  constants  ki
and k2 have been determined as a function of
temperature, in the range of 180 to 230  C,
and acid concentration, in the range  of 0.2
to 1.0 percent. The reaction  time for  maxi-
mum sugar yields  was  determined from the
model.
   A plant design for the  hydrolysis and  an
economic analysis based on the kinetic  model
indicate that sugar can be produced for be-
tween 1.8 to 3.0 cents/lb. This is in the range
to be competitive with sugar from molasses.
The  major  factors affecting  the  economics
are the plant capacity, the percent cellulose
in the refuse, the dumping fee, and the solid-
to-liquid ratio of the paper slurry feed  to the
reactor.
   A small, tubular,  continuous, isothermal
reactor  was constructed to study the operat-
ing parameters and further improve the eco-
nomics  of the  final plant  design. The effect
of impurities in  the refuse on the hydrolysis
and the fermentation of the sugar to alcohol
was  studied.
 82

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                   Laser-Mediated Lignin Solid Waste Fermentation
                       Dr. Donald A. Klein
               Department of Microbiology
                    Oregon State University
                  Corvallis, Oregon  97331
 Grant No. EC 00278-02
 Funds Awarded: $33,689
 Project Period: June 1,  1968 to May 31,  1971
OBJECTIVES:  To  determine  the  effects  of
laser and irradiation energy  sources on the
configuration of lignin substrates and to eval-
uate biologic effects of such modification proc-
esses.  Process are being  developed by  which
the lignin polymer  can be  degraded  com-
pletely  for  use as  a carbon  source   or  be
modified  by  microbial  transformations  to
yield  chemical  intermediates of commercial
interests.

APPROACH:  Initial  studies  were  concerned
with photolytic effects on microbial fermen-
tation  of model compounds  of which it  is
thought that lignin  is composed. The  photo-
lytic irradiation interaction with model sub-
strates was conducted with mercury arc  photo-
lytic energy. Areas of the ultraviolet, visible,
and near infrared spectrum, were investigated
by  the use of appropriate filters. After treat-
ments  at various  times and  temperatures,
analytical procedures were used to detect pos-
sible changes  in configuration,  linkages, and
sulfur state. After this treatment, enrichments
from  soils,  sewage,  and rotted woods were
used to develop competent cultures, followed
by  fermentation and chemical analysis.
  In  the  next  phase, a  laser  unit  producing
energy  at the  wavelength  determined opti-
mum in  the study  with mercury  arc  lamps
is being  used.  The laser  energy  source  is
coupled with a fermentation  vessel and used
for the study of batch fermentation by specific
organisms, to  allow study of the physiologic
aspects of use of photolysis product.

FINDINGS:  During this  research period, defi-
nite improvement in biological  availability of
lignin-sulfonate by  use of  photooxidative
modification has been  shown.
  Work  with  both  fungal  and  bacterial
growth systems in pure cultures  indicated that
photolysis during low or high pH conditions,
in comparison with pH 7.0, permits retention
and utilization of a greater portion of lignin-
sulfonate carbon. By use of varied photooxi-
dative  conditions,  it  has  been possible  to
render  residual  ligninsulfonate  carbon  as
much as 60 percent bioutilizable in one proc-
ess step.  Without  photolytic  modification
negligible bioutilization  is observed. Maxi-
mum bioutilizability  is  observed after  de-
coloration of the ligninsulfonate solution.
   Research of  this period has also given in-
formation germane to the present and future
design of lasers to be used in such processes.
Light wavelengths  of  less than 210  mm are
required, and as little  as 0.5  watt of output
power should give the potential for an efficient
single-pass treatment system.
   Information  on the nature of biologic re-
sponses to photooxidized ligninsulfonates has
also  been obtained. Fungi appear to utilize
lower weight polymeric products from earlier
photomodification as well as aromatic lignin
subunits, while bacterial  responses appear to
be related  primarily  to  the  utilization  of
aromatic subunits produced in later stages of
the  photooxidation process.  Microbial eco-
nomic utilization  coefficients  with photolyti-
cally produced ligninsulfonate fragments can
be equated to  use of conventional  carbon
sources at the beginning and end of the photo-
lysis period.
   Judged on presently available information,
further applications of this research can  be
considered.   These  biologically  improved
ligninsulfonates will be amenable to efficient
degradation in waste  treatment plant and
lagoon systems and also will be available for
production of single-cell protein. In addition,
this  treatment approach can be  applied  to
diverse  lignin-containing materials  and also
to pesticides and chemical wastes. This solid
                                                                                        83

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waste utilization approach can become a ma-
jor factor in creative management of recalci-
trant waste products.

                PUBLICATIONS
KLEIN, D. A., J. P. ELDRIDCE, and R. C. ROCKHILL. Photo-
fermentation of recalcitrant  molecules:  Initial studies
with  lignin  sulfonate , and lignin model compounds.
Bacteriological Proceedings, 69:16 (A105), 1969,  (Abstract.)

KLEIN, D. A. New  weapon for anti-pollution  arsenal.
Oregon's  Agricultural Progress, 16(l):6-7,  1969.

KLEIN, D. A., R. C. ROCKHILL, J. P. ELDRIDGE, and J. E.
PARK.  Fungal  and bacterial responses to  photooxidized
lignin  sulfonate substrates. Tappi, 53 (8): 1469-1472, Aug.
1970.
                  Noncombustive  Disposal of Solid  Agricultural Wastes
                           Dr. Ellis F. Darley
     Statewide Air Pollution Research Center
                     University  of California
                Riverside, California  92502
  Grant No. EC 00255-03
  Funds Awarded: $216,339
  Project Period: Feb. 1,  1967 to  July 31, 1970
 OBJECTIVES:   To determine the feasibility of
 shredding woody  wastes and incorporating
 them  into  the soil  and to evaluate  the re-
 sulting effect  of this  practice on soil-borne
 plant pests, soil properties, and eventual plant
 growth. Specifically,  to determine  whether
 adding wood  chips to  the  soil  in  various
 orchards increases the  inoculum potential of
 the root rot  fungi Armillaria  mellea  and
 Phytopthora  spp.  and  of  the wilt  fungus
 Verticillium alho-atrum and  favors  the re-
 production of the shot-hole borer, soil struc-
 ture alteration, and  water penetration.


 APPROACH:   Mechanical shredding operations
 were  carried  out at  several  demonstration
 plots,  the time and costs of these operations
 and the effect  on soil chemistry being  em-
 phasized. Laboratory  and  field experiments
 were performed to determine the effect of the
 addition of the shredded waste on fungi  and
 diseases in  the vegetation and to investigate
 their control  by chemicals.  Special  attention
 was given to the effects of climate, differences
 in  plant species, and the rate  of decay of the
 shredded material.
FINDINGS:   Shredding  experiments  were  es-
tablished  in 21  orchards  representing the
major fruit crops in central portions of Cali-
fornia. The  biological  processes  evaluated
after incorporation  of  waste  into  the soil
require considerable time before changes can
be noted. Only two seasons' wastes have been
chipped and turned into the soil, and no con-
clusive results are yet available. Certain trends
have, however,  been noted.
   Most  of  the incorporated waste is  found
in the top 4 to 5 in., but  occasionally pieces
are found as deep as 8 to 10 in. A few pieces
the size  of a  man's thumb have been  found
to be  infested with Armillaria, and the fun-
gus was  viable. Although  the numbers  in-
volved  were small, the  results indicate that
such pieces can be infested and thus present
a  potential threat in increasing rate of  spread
of the  fungus.  No fine  chips  have  ever  be-
come  infested, either in  field trials  or  in
special  experiments  where  the material was
buried  by  hand  and  inoculated  with  the
fungus. In the latter experiments,  Armillaria
easily  infested pieces 4 in.  long  and varying
from yz to 2 in. in diameter.
   While  laboratory studies have  shown that
Phytophthora can infest nonsterile wood chips,
isolations to date  from  field plots have not
shown any significant change, either  an  in-
crease or a decrease in the inoculum potential.
   A significant preliminary result with Verti-
cillium is that  when infected  olive branches
were chipped and added to the soil, no con-
tamination of the soil occurred.
   One  aim of  the insect studies was to pre-
 84

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vent  the  generation 'of  orchard wastes,  as
would be  the case when borers attack healthy
tree  branches.  Preliminary work has shown
that  latex paint applied to branches prevents
the insects from laying eggs.
  An interesting observation  has been made
on soils contained in large cylinders, some of
which have received shredded wastes. Follow-
ing heavy rains, soils without chips had water
standing on  the surface  for at least 24 hr.
No water was standing on treated soils.  In
other experiments, differences  in water re-
lease  properties and  hydraulic conductivity
indicate  that a  change  in irrigation  practice
may be  needed to manage  properly fields
treated with  wood waste additions.
         Photosynthetic  Reclamation of Agricultural  Solid  and  Liquid Wastes
                     Dr. William  J. Oswald
   Sanitary Engineering  Research  Laboratory
           University  of  California—Berkeley
                Berkeley,  California  94720
  Grant No.: EC 00272-03
  Funds Awarded: $93,838
  Project Period: June 1, 1967 to May 31, 1970
OBJECTIVES:   To study the application of an
integrated system involving an anaerobic di-
gestion phase and an algae production phase
to the  disposal of  agricultural wastes,  espe-
cially animal manures, and to the reclamation
of the  plant nutrients and  water contained
in the waste.

APPROACH:   A plant consisting of a digester,
algae pond, equipment for harvesting algae,
and  necessary ancillary equipment was assem-
bled  at  the  University of  California,  Rich-
mond Field Station. Animal wastes were fed
to a  150-gal  concrete  anaerobic digester  and
fermented. The effects of solids content, pH
of the waste,  temperature, detention period,
loading, and method of operation  on  the di-
gestion process were determined with animal
wastes.  Wastes were characterized not only
on  the basis  of origin but  also  on that of
C/N  ratio, nitrogen  content,  pH, and  total
and  volatile solids content.  The digester was
operated  both as a batch process and as a
continuous  process  to determine digestion
efficiencies under  both conditions. Digester
performance  was judged on the basis of gas
production, extent  of volatile  solids destruc-
tion,  pH, volatile acid concentration  of the
sludge, and the physical characteristics of the
sludge.
  The effluent from the digester was  fed di-
rectly  into a 5,500-gal variable-depth algae
pond.  The  effects of temperature, detention
time,  culture  depth,  mixing  time,  type of
waste effluent, and CO2 concentration on algae
growth were determined. The performance of
the  pond was evaluated  on its overall con-
version efficiency and by its effluent quality
after the algae had been removed. The algae
were harvested by methods proved practical
and economical in  previous  research,  i.e.,
initial concentration,  dewatering, and final
drying.

FINDINGS:  In  choosing a subject  for the  first
phase  of the  research  project from among
the  various  solid waste  producers  in food
production, it  was decided to select chickens,
i.e.,  egg  production  hens, because of the rel-
ative ease of housing and  rearing them,  and
equally importantly,  because  the  disposal of
chicken manure constitutes a major problem
not only in California but also in  many other
States. Accordingly, the objectives and proce-
dures  outlined in the previous section were
directed  toward the management of chicken
wastes.
   Early in the study, it became apparent  that
to ensure a reliable  and uniform source of
manure  for  experimentation,  it  would  be
necessary to install a colony of egg layers at
the site of the study. Therefore, a 14- by 14-ft
poultry  enclosure  was  designed and con-
structed  and was  stocked with 113 20-week-
                                                                                       85

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old white leghorn pullets caged in batteries,
each of which held four hens (0.45 sq ft/hen).
A Fiberglas-coated trough  was placed below
each  row of  batteries to catch the  chicken
excreta.  Once each  hour  a tipping  bucket
(8.3-gal capacity) mounted at the end of each
of the troughs discharged its contents (water
from the algae pond)  into the trough to flush
the excreta  down the trough and into a sedi-
mentation  tank.  It was  important that the
wet  weight of  manure  solids in the  slurry
discharge into the sedimentation tank be less
than  3 percent of the slurry weight (manure
plus water). At this or smaller concentrations,
more than  70 percent of the solids settle out
of suspension in less than 15 minutes. A sub-
merged sump  pump  moved the supernatant
from the  sedimentation  tank  to  the  algae
pond, and  a  slude pump moved  the settled
solids to  an anaerobic digester. Supernatant
from the  digester was  discharged  into the
algae pond, while the digested sludge periodi-
cally was wasted to  the environment.  Pond
culture either was recycled directly to the
tipping  buckets  or  was  first  processed for
algae removal and then discharged into the
tipping buckets. Provision was made for dis-
charging  the  overflow when necessary.  Tap-
water served as drinking water for the  hens.
The overflow from the drinking water troughs
was  discharged into the manure troughs and
thereby served  the dual purpose  of  keeping
the troughs moist and of constituting makeup
water. During the winter months, when algal
growth was negligible, a  sump pump with
an above-the-surface  discharge  served as an
aerator to keep the pond aerobic and thereby
prevent the development of odor  nuisances.
   At the time of  this writing,  the indicated
required pond area per bird was 2 sq ft.  With
the  pond depth at 12 in.  or  less, and water
being allowed for in  the digester, sedimenta-
tion  tank,  and  tipping buckets,  the water
needed to establish the overall system would
be about 15  gal/hen. The  amount of water
needed to maintain  the system, once it was
established, would be a  function of  evapora-
tion  plus spillage minus overflow from the
drinking  water troughs.
   At an  average detention time of  23  days,
gas production was about 12 cu ft/lb volatile
solids introduced. Although low at first, the
methane content of the gas steadily increased
until at the time of this writing it constituted
from 50  to 60  percent of  the gas.  Overall
volatile solids  destruction was about 55 per-
cent. Of the total solids input, approximately
70  percent  was  converted   to  digester gas.
Only a fraction  of the  algae growing in  the
pond was harvested. Harvesting was done by
"natural" settling and by centrifugation. The
potential algal yield in  the pond was equiva-
lent to 30 to 40 tons (dry wt)  of algae/acre-
year.  Overall  photosynthetic  conversion  of
visible light energy to algal  cellular material
ranged from 0.64 to 2.8 percent.
  An  analysis  of the integrated system indi-
cated  that biological activity in the sedimen-
tation tank, digester, and algae pond decreased
the  total solids  by  60  percent; the volatile
solids by  62 percent;  the  total  unoxidized
nitrogen by 45 percent; and  the energy  input
(exclusive of light) by 56 percent.
  An  economic  evaluation based  on an inte-
grated system  of 100,000 egg layers  and  the
application of the low loadings and the high
cost  and overdesigned  components  used  in
the research indicated that the waste-handling
costs of  the system  would be at  the  most  2
cents per dozen  eggs. If the value of the algal
crop were credited to the operation, the  net
waste-handling cost  would be 1 cent or  less
per dozen eggs.

                 PUBLICATIONS
GOLUEKE, C. G.,  and  S. A.  KLEIN. Treating combined
liquid and solid wastes. Presented  at 1968 Conference of
California Water Pollution  Control  Association, Santa
Rosa, April 24-25, 1968. 15 p.
ICHIKAWA,  K., C.  G. GOLUEKE, and W. J.  OSWALD.  Bio-
treatment of Steffen House waste.  Journal  of the Amer-
ican  Society  of Sugar Beet  Technologists,  15(2):125-150,
July  1968.
DUCAN, G. L., C. G. GOLUEKE, and W. J. OSWALD. Photo-
synthetic reclamation  of agricultural  solid and liquid
wastes. Presented at Engineering  Foundation  Research
Conference, Solid  Waste Research  and Development, II,
Beaver Dam, Wis.,  July 22-26, 1968. Conference  Pre-
print No.  E—1.
DUCAN, G. L., C. G. GOLUEKE, and W. J. OSWALD. Photo-
synthetic reclamation  of agricultural  solid and liquid
wastes.  Presented at  42nd Annual Conference, Water Pol-
lution Control Federation, Dallas,  Oct  5-10, 1969. 13 p.
GOLUEKE, C. G. Chemical and microbial characteristics of
in ban solid wastes. [Presented at Annual Meeting, Amer-
ican  Society for Microbiology, Miami  Beach, May  4-9,
1969.] 17 p.
 86

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                       Poultry Offal Silage  as a  Feed Ingredient
                         Dr. Charles H.  Hill
               Department of Poultry Science
            North Carolina State  University
             Raleigh, North Carolina  27607
 Grant No.  EC 00269-02
 Funds Awarded: $32,991
 Project Period: June 1, 1968 to May 31, 1970
OBJECTIVES:  To develop  a method of pro-
ducing  and using  silage  from  poultry  offal
(slaughtering wastes including intestines and
contents, the feet, and the  head) as a feed for
chickens.

APPROACH:   Poultry offal  silage is  presently
prepared by mixing ground offal with a source
of carbohydrate, usually corn meal, and water
and letting it sit for 1 week. No specific  at-
tention is paid  to the  kinds  of  organisms
present. This research effort investigated the
possibility of improving the  nutritive value
of the silage. One approach was to investigate
the effect  of various carbohydrate sources and
the resulting predominance of  particular  or-
ganisms that utilize them.  When a particular
organism  was found to be well suited to the
production  of  a good  silage,  that  organism
was isolated, developed, and  inoculated into
a  sterilized mixture before  fermentation  to
determine if uniformly superior silage could
be produced from  a nutritive standpoint.
   The criterion of nutritive  quality was the
performance of the silage  in  feeding experi-
ments. A  standard  soybean meal-corn ration
enriched  with  all  the known required vita-
mins and minerals was added to this ration
at the expense of corn,  since the silage and
corn  have approximately  the same protein
content.  Attention was  paid  to  keeping the
energy levels of both diets equal by  adding
fats to the basic diet to offset the  extra  fat
contained  in the  silage.  Chicks  were  fed
both  diets from the  day  of hatching, and
the growth rates of the chicks were used as
an evaluation of nutritive quality. As prepara-
tions  of  the  silage  were made, samples were
taken, and the value as a feed ingredient was
assessed from its content of known nutrients.

FINDINGS:  When poultry  offal silage  is used
as a part of the corn-soybean meal basal, a
growth response of 5 to 10 percent  has been
obtained. Supplementing the diet with anti-
biotics, zinc,  and molybdenum or increasing
the known vitamin  levels do  not  increase
chick growth under these conditions. In a field
trial with chicks raised  under practical con-
ditions a growth response  of 6.8  percent was
obtained. The  chicks were raised to  market
weights at 8 weeks  of age. The growth stimu-
lant is water soluble, but efforts  to  extract it
with organic solvents have  been unsuccessful.
It is stable to autoclaving at 15 Ib pressure
for 30 min.
                           Radiolytic  Hydrolysis of  Cellulose
                          Dr. James L. Kelly
            Nuclear Engineering Department
                      University of Virginia
             Charlottesville, Virginia  22901
 Grant No. EC-00362-01AI
 Funds Awarded: $25,707
 Project Period: Feb. 1,  1970 to Jan. 31,  1971
OBJECTIVES:  To  determine  the  effect  of
gamma radiation on the hydrolytic conversion
of cellulose to  fermentable sugars. To deter-
mine the feasibility of using radioactive wastes
                                                                                       87

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as intense gamma radiation sources for large-
scale irradiations of cellulosic  materials.

APPROACH:   Initially  a   gamma  radiation
chamber will be  designed and  constructed to
facilitate the study of irradiation hydrolysis.
The effects  of  irradiation dose, dose rate,
chemical environment, and temperature on
the hydrolysis  of various  types  of  cellulose
to produce fermentable sugars will be deter-
mined.  The effects of these parameters on
the rate of decomposition of the fermentable
sugars  produced in  the  hydrolysis reaction
will also be determined. The effect of irradia-
tion on the  hydrolysis reaction  will also be
determined and related to the  time at which
it is applied—before or during the chemical
hydrolysis reaction. As a result of these deter-
minations, conditions for optimum sugar pro-
duction will  be denned. The second portion
of this project  is related to solving problems
associated with the use of radioactive  wastes
as the gamma radiation source. The amounts
and associated activities of the various radio-
isotopes  produced as fission products  in the
nuclear power  industry in years to come will
be estimated. The most practical form of the
gamma radiation source is being determined,
and a facility will be designed in accordance
with Atomic Energy Commission criteria for
the storage and use of these wastes.

FINDINGS:  This  grant  was awarded  on Feb.
1, 1970, and findings are not yet available.
                     Reclamation of  Energy  from  Organic  Refuse
                         Dr. John T. Pfeffer
            Department of Civil  Engineering
                        University of Illinois
                     Urbana, Illinois  61801
  Grant No.  EC-00364-01
  Funds Awarded: $40,390
  Project Period: Aug. 1, 1969 to July 31, 1972
 OBJECTIVES:   To  determine  the  operating
 parameters  for the  biologic  conversion of
 organic  solid  waste  to  methane by use of
 anaerobic digesters. To evaluate the potential
 operating problems associated with  the  pro-
 posed process and determine the potential for
 energy reclamation.
APPROACH:   The effects of  operating tem-
peratures, retention times, and solids content
are  being  determined  and  related  to the
energy yield from the methane fermentation,
the reduction in quantity of organic refuse,
and the characteristics of the residue. Fifteen-
liter plexiglass digesters will be  used for the
laboratory study. Digester  temperature  will
be closely controlled, and mixing will be pro-
vided  by  mechanical  stirrers.   Residential
refuse will be used as collected with no sepa-
ration of the noncombustibles,  plastics, and
rubber  before it is  placed  in   the  digester.
 Initial runs will be made at 35 C to determine
 the  solids content in the  feed  required  for
 the optimum production of methane. Similar
 studies will be conducted at temperatures up
 to 60 C.
   Control of the  digestion  process  will  be
 based  on the pH,  the concentration  of vola-
 tile  acids, and the gas production.  Daily  gas
 production will  be measured and  the com-
 position of the gas determined. The pH will
 be maintained in the optimum range of  6.6
 to 7.6. No attempt will be made to control  the
 volatile  acids,  except  during  the  startup
 period, at which time  the loading  will  be
 controlled to keep the  volatile  acid  concen-
 tration less than 2,000 mg/liter.
   Process  evaluation  will  be based  on  the
 efficiency  of  the  conversion  of the  organic
 solids to methane gas and on the energy value
 of the resulting gas mixture. Solids balances
 will be  run  on the systems and correlated
 with methane production.
 88

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FINDINGS:   Progress to date has been limited
to constructing the  laboratory units, obtain-
ing the shredded domestic refuse from  the
BSWM's Center Hill Laboratory, and analyz-
ing the  chemical characteristics of this refuse
prior to starting the experimental runs.
                Refuse  Reclamation by Size Reduction and Separation
                       Dr. David  G.  Wilson
      Department of Mechanical Engineering
        Massachusetts Institute of Technology
          Cambridge,  Massachusetts  02139
 Grant No. EC 00333-01
 Funds Awarded: $62,685
 Project Period: June 1,  1969 to May 31, 1971
OBJECTIVES:  To demonstrate  the feasibility
of separating refuse into  several components
in an  automated manner partially through
the use of  a  vortex classifier  mill to effect
both size reduction  and coarse separation. A
subsidiary  aim is to determine  which com-
ponents  of refuse  may  be separated with
maximum  benefit-cost ratio.

APPROACH:  This project consists  of seven
phases of research,  some  of which run con-
currently.  The  first phase,  which  runs  for
the 2 years of the project, will investigate a
vortex classifier  and  its  ability  to  provide
partial size reduction and coarse classification
of refuse  components.  During  the  second
phase, salvageable refuse  components  will be
identified  and  listed  with  present  typical
gross salvage values. The  various  refuse com-
ponents' properties  will be identified  during
the next phase of the  project. Among these
are density or specific weight,  thermal con-
ductivity, radiation  emissivity,  dielectric con-
stant, paramagnetism, gamma-ray absorption,
and  drag coefficient. A search  will be con-
ducted  to  find  the minimum   number  of
sensors  that positively  identify all  the com-
ponents  of refuse  listed  in phase  two. A
preliminary design of a hypothetical  separa-
tion  system will  be made in phase four.
  The  plant  will  be  designed  to pass  the
refuse  through a series of sensors  and pro-
vide a means of removing  the  refuse com-
ponents into various categories. During phase
five a cost  benefit analysis of various  systems
designed to remove  different refuse  compo-
nents is being made.
  Phases six and seven deal with the design
and construction of a  75  ton/day pilot plant
to accommodate virtually all the types of trash
currently  found in  municipal refuse. These
phases are not part of the  currently funded
effort. It is envisioned that a maximum num-
ber of categories of refuse will be separated
in the  pilot plant so that each  sensor and
removal device can be evaluated.
FINDINGS:
  1. The  vortex  device does not seem to be
of much value as a pulverizer of general mixed
refuse. It  does seem to work well with brittle
materials, e.g., glass,  or with  paper  or  tex-
tiles.  We  believe  from our model tests  that
its  value  will be  greater as a classifier,  and
we  are designing a test rig  to investigate the
flow  patterns of  the  air  and  the particles
(modeling these as the flow of dense particles
in water)  so  that we may later design a half-
or full-scale classifier.
  2. We believe  that we have two promising
approaches to mechanized sorting. One is the
method suggested in our proposal, whereby
shredded  refuse would be scanned by  a series
of sensors and a  decision would be made on
the basis of the readings obtained about which
of several categories  the material  would be
switched to.  We  have found that microwave
and infrared sensing shows promise, and we
are investigating  further. The second method
is applied to unshredded single items of refuse,
e.g., a bottle, or  a newspaper, or a  can. A
signature  is obtained from a sensor that reads
a mix of properties and characteristics.  We
                                                                                       89

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have found that the readings from an acceler-
ometer attached to a  ball dropped onto each
item gives enough information to permit cod-
ing of most useful and nonuseful items. We
are pursuing this line of approach vigorously.
  3. We have made a preliminary economic
analysis,  which seems  to indicate that a rec-
lamation  plant should  be  a  favorable  al-
ternative to an incinerator when the alterna-
tive costs of disposal are high, e.g., $10. This
figure will come down when mechanized sort-
ing is  available and will  come down more
when governmental action prevents wild fluc-
tuations in  the price of secondary materials.
                      Single-Cell  Proteins from  Cellulosic  Wastes
                    Dr.  Clayton  D.  Callihan
         Department of Chemical Engineering
                   Louisiana State University
              Baton Rouge, Louisiana   70803
 Grant  No.  EC 00328-02
 Funds  Awarded: $190,157
 Project Period: Mar.  1, 1969 to Feb. 28, 1971
OBJECTIVES:   To  isolate and  identify cellu-
lose-digesting organisms, to study the growth
of these organisms in the presence of cellu-
lose, and to investigate the optimal conditions
for enzyme production during growth of the
various cellulosic wastes.  Once suitable  or-
ganisms  were isolated, a  chemical-microbial
pilot plant was operated  to convert  various
cellulosic wastes to  single-cell proteins. The
nutritional value, digestibility, and toxicity of
the single-cell protein are being determined.

APPROACH:  Before the research grant award
an  organism was  isolated  that is   capable
of breaking  down cellulose. This  organism
was used as the model organism for designing
the initial stages of the pilot-plant studies. A
search  is  being made  to isolate other  or-
ganisms capable of utilizing cellulose. These
organisms are grown in the presence of sub-
strates prepared from  cellulosic wastes such
as bagasse, rice straw, wheat straw, and paper
wastes so that the organisms capable of metab-
olizing the various wastes can be determined.
  With use of BSWM  contract funds, a con-
tinuous chemical-microbial plant was designed
and constructed for  the production of single-
cell protein.  The process consists of an initial
size reduction unit,  a mixing area where the
cellulosic wastes are  pretreated with  sodium
hydroxide, an  oxidation  step whereby the
lignin is  deploymerized, a sterilization  step,
an acid neutralization step, and finally fermen-
tation. Techniques for refining and processing
the  cell  yield  are being developed and  de-
signed with the necessary amount of flexibility
to ensure optimum conditions.
  The untreated  whole cells, disrupted cells,
and various protein fractions derived from the
cell  are  evaluated both chemically and bio-
logically. Chemically, the  nitrogen content,
protein  content,   amino  acid composition,
lipid composition, and  vitamin and mineral
content  of the cells are determined. A study
with rats is determining the toxicity, digesti-
bility, and nutritional value of the harvested
cells.
  The   chemical-microbial  pilot  plant  has
been constructed  and is  being operated at
NASA's  Mississippi Test Facility.

FINDINGS:  A  cellulose-decomposing  aerobic
and mesophilic bacterium  has been isolated
from the soil of a sugar cane field and  identi-
fied as a member of the genus Cellulomonas.
This bacterium   produces  the cellulase  en-
zymes that cause subsequent hydrolysis of the
cellulose to simple sugars. These hydrolytic
products then serve as the substrate for micro-
bial growth. The microbial cells are harvested
for their protein, and this  product  is usually
referred  to as  single-cell proteins. The enzy-
matic hydrolysis of cellulose is not new. E. T.
Reese and  R.  G.  H.  Siu,  as well  as  others,
 90

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have  studied fungal  cellulases  extensively,
but the growth rates of fungi are many orders
of magnitude slower than  those of bacteria
and  furthermore,  the amount of protein is
considerably less  in  fungal products.  Since
production  costs vary directly with growth
rates this would indicate that the use of bac-
teria to dispose of cellulosic wastes may be a
more practical approach.
  When bagasse, the residue from sugar cane
after the sugar is  extracted,  is used  as the
sole  carbon source for the  growth of Cellu-
lomonas,  a yield of 20 Ib of cell product is
obtained  for each 100 Ib of feed. About  50
percent of the bagasse is cellulose. Approxi-
mately  75 to 80 percent of this cellulose is
solubilized by the microorganisms. Of this
37.5  to  40 Ib of cellulose consumed from the
initial   100 Ib, about  50 percent  is used  to
satisfy the metabolic requirements of the liv-
ing cells. The remainder is converted to cell
mass.
  The  harvested cells are about 50  percent
protein, and the amino acid analysis shows
that  this protein is high in lysine and other
essential amino acids that are usually deficient
in vegetable proteins. A comparison  of the
amino acid pattern of Cellulomonas with the
ideal  amino acid  profile  recommended  by
FAO shows that our  product compares quite
favorably.
  Feeding studies on male weanling rats have
shown that the limiting amino acid in our
cells is  1-methionine.  When the rats were fed
ad libitum or an otherwise adequate but pro-
tein-free diet or the same basal diet contain-
ing various amounts of these intact cells, they
showed definite weight  gains  above the  20
percent  level of supplementation.  Rats fed
with cells enriched with 0.5 percent 1-methi-
onine showed  improved  growth rates.  Rats
fed for  several weeks  at the 70 percent cell
level  showed none of  the toxic  responses
normally associated with high  nucleic  acid
levels. Prehydrolysis of the  cell walls or cell
wall rupture by homogenization improved the
overall  digestibility  of the  protein  product.
Other feeding studies on rats,  chicks,  swine,
and cattle are now underway.
  The economic feasibility of producing pro-
teins from the  cellulosic portion  of  urban
solid waste depends to a large extent on the
growth  rate  of  the  microorganisms.  To  im-
prove this aspect of the problem, a  study is
underway on methods of improving the kine-
tics of cell growth. Initial results of this study
have shown what was known all along, that
very few natural processes occur rapidly with
a single pure organism  but instead  proceed
by using several organisms,  each with a func-
tion that hastens the overall process.
  In this work it was found that the rate of
cell production was  being limited by  a build-
up  of cellobiose in  the menstrum. This  was
apparently giving feedback inhibition or allo-
steric inhibition as  it is sometimes called. A
second  organism was then found that  was
quite specific for ft  glucosidase. This bacter-
ium, genus Alcaligenes and species Faecalis,
was grown symbiotically with  Cellulomonas.
The end result has been a nearly  five-fold
increase in growth rates. Surprisingly, the Al-
caligenes does not propagate itself  to a large
extent and is found to represent only  about
7 to 8 percent of the final cell mass.
  A chemical microbial pilot  plant  was de-
signed and built to  produce proteins by  this
technique and to check our laboratory find-
ings on  a larger scale. Considerable operating
information is being obtained from this unit.
The large unit was built at NASA's Missis-
sippi Test Facility.  Since the facility  is large,
we  can check out much more  precisely  the
important economic aspects of our  process.
Several  difficulties have been  observed that
were not  apparent in laboratory research.
  One  of the  most difficult  problems  en-
countered  in the  pilot  plant  has  been  the
metering  of  dry solids into the continuous
system.  Very precise metering is necessary to
obtain  careful  material  balances  that will
help determine the economics of the  process.
  Difficulty has also  been encountered in the
large  unit,  cell concentrations  being  much
smaller  than expected. We are obtaining only
about 1 g of dry cells  per liter of  effluent
from the fermenter.  This is considerably  less
than the  design concentration of 6  to 7  g/
liter.
  A careful analysis  of the cause of the small
cell concentrations has led us  to believe that
the  Ci  enzymes are induced and not con-
stitutive as  originally presumed. If  one  ex-
amines  the  growth  curves of Cellulomonas,
                                                                                       91

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they show a distinct log phase of cell growth
that does  not  reach a  completely stationary
phase as most  cells do  but instead  gradually
increases with  time.
  During  the  initial alkali pretreatment  of
waste  cellulose,  about  20  percent  of  the
original cellulose is  solubilized.  We have in-
terpreted this  information  to  mean that  the
cells are feeding  on this product during  the
log phase  of cell  growth and  that only after
most of the soluble  carbohydrates have been
consumed do the Ci and Cx enzymes become
very  active.  The  gradual  increase  of cell
growth during the  stationary phase is  the
result of  the gradual induction of the com-
plete enzyme system.
  We have finally  concluded  that  the best
way to induce fully the Ci and Cx enzyme
system in a continous  process is to  go to a
two-stage fermentation. In this system all the
soluble carbohydrates should be consumed in
the first  fermenter, and the second  fermenter
should then contain a well-developed cellulase
system of enzymes that  should lead  to utiliza-
tion of the remainder  of the  cellulose.
  An  economic analysis has been  projected
based  on  a plant, to produce  100  tons  of
protein product per year for recycle through
animals. This analysis shows that the product
cost should be competitive with soy bean pro-
tein if the cell concentration can be increased
to  6  to 7  g/liter and if the  two-stage  fer-
mentation gives the anticipated growth rates.


                PUBLICATIONS

HAN, Y. W., and V. R. SRINIVASIN. Isolation and charac-
terization of a  cellulose-utilizing bacterium.  Applied
Microbiology, 16(8):1140-1145,  Aug. 1968.

CALLIHAN, C, D., and C. E. DUNLAP. The economics of
microbial proteins produced from cellulosic wastes. Com-
post Science, 10(l-2):6-12, Spring-Summer  1969.

DUNLAI", C. E., and C. D. CALLIHAN. Fermentative utiliza-
tion of sugar cane bagasse. Unpublished data, Louisiana
State University,  Baton  Rouge. [Presented at  Meeting,
American Society of  Sugar Cane Technologists, June 5,
1969.]

HAN, Y. W.,  H. A. SHUYTEN,  JR., and C.  D.  CALLIHAN.
The combined effect of heat and alkali for sterilizing  bac-
terial  spore  in sugar cane bagasse. Presented at South
Central  Branch  Meeting, American  Society for Micro-
biology,  New Orleans, Nov. 21-22,  1969. [24 p.]

HAN, Y. W., and V. R.  SRINIVASIN. Purification and char-
acterization  of Beta-glucosidase of Alcaligenes  faecalis.
Journal  of Bacteriology, 100(3):1355-1363, 1969.
                    Studies on Modifications of Solid Industrial Wastes
                    Dr. Cornelius S. Grove Jr.
                Civil Engineering Department
                          Syracuse University
                 Syracuse, New York  13210
  Grant No. EC 00257-02
  Funds Awarded: $157,518
  Project Period: Feb. 1, 1969 to Jan. 31, 197T
OBJECTIVES:  To determine the physical and
chemical properties of major process chemical
industries' solid wastes and to study modifica-
tions of these properties that will permit  re-
habilitation and  beautification  of the pres-
ently barren land areas covered by deposition
of these wastes.

APPROACH:   To meet the objectives the  fol-
lowing coordinated program is being carried
out: (1) Collect and  collate the available  in-
formation on the physical and chemical prop-
erties  of various solid industrial  wastes from
chemical process industries to determine com-
mon characteristics and  variants; choose a
typical solid industrial waste for  analysis and
classification of the physical and chemical con-
stituents and determine their consistency.  (2)
Study methods and rates  of infiltration,  per-
colation, and leaching, under simulated  nat-
ural conditions, for removal of chemical  con-
stituents known  to be  harmful  to desirable
vegetation.  (3)  Investigate modifications of
solid industrial wastes  by mechanical  manip-
ulation  and by  chemical  treatments  to alter
the  "soil" properties so that desirable  vegeta-
92

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tion can be grown; tes,t optimal modifications
in small "flats" in the laboratory and in small
plots in situ.

FINDINGS:  Evaluation and summarization of
the accumulated data have shown the exceed-
ingly broad scope of the solid wastes problem.
It has been demonstrated that personal solici-
tation through letters and interviews is very
frequently necessary to obtain adequate  re-
sponse,  not only from  individual  industries,
but  also from national organizations. Signifi-
cant data reinforce conclusions that the scope
of the total solid waste problem in quantity is
7 to 10 times the quantity of municipal solid
wastes (frequently quoted as 2 to 1) and that
the varied quality of solid wastes necessitates
a  multifold approach  to  handling and  dis-
posal methods.  Too little attention  is cur-
rently being paid to reclamation values and
reuse possibilities of many varieties of solid
wastes.
   The  specific solid waste  chosen for initial
experimentation arises from  Solvay  process
productions of  soda ash  (sodium  carbonate)
utilizing raw materials of limestone and salt.
In various localities, large areas of land have
been used for deposition of the solid wastes
from  this chemical process. Removal of solu-
ble salts is slow (many years—20 to 100); re-
habilitation is inhibited by the salt content's
preventing growth of suitable  cover  vegeta-
tion and by the lack of suitable load-bearing
characteristics, which causes settling of struc-
tures, noticeable even under reinforced  high-
ways. The major  conclusions  from present
experimental studies are as follows: (1) Leach-
ing of the soluble salts is feasible  but  slow,
even  if  the necessary subsurface drainage  sys-
tem is provided.  (2) Vegetation will develop
in top soil placed over the waste bed material
if proper drainage is maintained so that leach-
ing continues to  overcome capillarity.
  Research  studies  are  being  continued on
this waste, and definitive investigations on the
chemical and biochemical reactions leading to
the so-called  coal mine  drainage and  the
leaching of synthetic fertilizing elements from
farm  lands are being initiated.
                PUBLICATIONS

GROVE, C. S., JR.,  M. L. KESTNER, and N.  L. NEMEROVV.
Rehabilitation of  solid industrial  wastes  disposal sites.
Presented at 24th  Annual Purdue Industrial Waste Con-
ference, Puidue University, Lafayette, May 6-8, 1969. 28 p.
                  Thermophilic  Aerobic  Process  for  Waste  Treatment
                       Dr.  John F.  Andrews
          Environmental  Systems Engineering
                                Department
                         Clemson  University
            Clemson, South Carolina  29631
  Grant No. EC 00268-03
  Funds Awarded: $89,738
  Project Period:  Aug. 1, 1967 to July 31,  1970
OBJECTIVES:   To study the application  of  a
thermophilic  aerobic-digestion process lead-
ing to the treatment  of  organic  wastes,  par-
ticularly ground solid wastes containing 3 to
5  percent garbage  solids  and primary  and
waste-activated sewage treatment  sludges. To
develop a theoretical mathematical model for
the process that  expresses temperature of the
reactor and concentration of the effluent sub-
strate as a function of the concentration, de-
tention time, and oxygen supply rate of the
input substrate.
APPROACH:   Ten-liter  continuous-flow reac-
tors  with provisions for mixing, flow varia-
tion,  air  injection, pH  determination,  and
effluent measurement  were used. The effects
of  temperature  and  detention  time  were
studied.  The  reactor effluent was studied by
analysis for substrate, cell mass, and carbon-
hydrogen-nitrogen content of the washed cells;
by photomicrograpy of the cells; and by anal-
ysis  for COD, effluent gas composition, and
dissolved  oxygen as close  to steady-state  con-
ditions as possible. The  last  phase of this
                                                                                         93

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project determined the effect of rapid changes
in the reaction mixture temperature on  the
process.
  A mathematical model for  the process that
expresses production of the effluent substrate
as a function of concentration, detention time,
and  oxygen supply  rate of the substrate  was
developed, initially from  theoretical knowl-
edge and, as research progressed, from experi-
mental  results.  Computer simulation studies
were made to  guide model development  and
experimental planning  and  to indicate  the
direction  of  future  pilot-plant  research.

FINDINGS:  Computer simulation  studies in-
dicate that the process would be feasible for
the  treatment of mixtures  of organic solid
wastes  and  primary  and   waste-activated
sludges.  Sufficient  heat  would be  generated
internally  in  the   process to  make it  self-
sustaining at temperatures of  100  to  130 F.
The process would have  the advantage over
other biologic processes of increased reaction
rates and increased  destruction  of organic
solids.
  The parameters for use in the model have
been  determined experimentally  for  simple
substrates. The  experimental  results prove
that the advantages  claimed are true for sim-
ple substrates. Preliminary results from exper-
iments and modeling efforts to  determine the
effect of  rapid  changes in reaction mixture
temperature  on the  process indicate the  vari-
ables (airflow  rate  and  solids  content)  that
have  the  greatest influence on  reaction  mix-
ture temperature and that should, therefore,
be controlled during process  operation.
  The process is now ready for  field studies at
a pilot scale with a mixture of garbage and
domestic  sewage sludge.

                PUBLICATIONS

KAMBHU, K., and J. F.  ANDREWS. Aerobic thermophilic
process for  the biological treatment of  wastes—simulation
studies. Journal of the Water  Pollution Control Federa-
tion, 41 (5,  pt. 2, Research  Supplement):R127-R141, May
1960.
KAMBHU, K., and J. F. ANDREWS. Mathematical model for
mixed cultures of thermophilic micro-organisms. Presented
at 62nd Annual Meeting, American Institute of Chemical
Engineers, Washington, Nov. 16-20, 1969.
                     Use of Domestic Waste Glass for Urban Paving
                        Dr.  Ward  R. Malisch
              Department of  Civil Engineering
                University of Missouri—Rolla
                  Columbia, Missouri  65201
  Grant No. EC 00329-01
  Funds Awarded: $32,653
  Project Period: June 1, 1969 to May 31, 1972
 OBJECTIVES:  To  establish  that waste  glass
 can be used  as  an aggregate in bituminous
 mixtures for  street maintenance and to  illus-
 trate this potential use as a method of solving
 urban glass waste disposal problems. To ac-
 quire engineering  data  on  bituminous-glass
 mixtures with respect to suitable gradation
 ranges for  the glass aggregate,  proper grade
 and type of asphalt to be used, and the range
 of  asphalt  contents satisfying stability, dura-
 bility, and workability requirements.

 APPROACH:   The first  of  the two  project
 phases consists of laboratory studies to deter-
 mine the properties of the glass  aggregate and
 bituminous  materials  that produce suitable
 paving mixtures. The  mixtures investigated
 include aggregates consisting entirely of glass
 as well as combinations of conventional min-
 eral  aggregates  and glass. Also included  in
 this phase is an investigation  of the degrada-
 tion  occurring  during compaction  of bitumi-
 nous mixtures containing the glass aggregates.
   Investgation  of the  type and grade  of bi-
 tuminous material  to  be used  centers upon
 adhesion  or stripping  tests and qualitative
 evaluation of the mixture's workability. The
 effect of variations in glass composition upon
 adhesion  is  being  studied.  Specimens   are
 fabricated  at  several  asphalt  contents  and
 94

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tested for stability, flow, compression strength,
void ratio, and stripping resistance.
  Phase  two of the study will be a field test-
ing program in which large batches  of the
bituminous-glass mixture will be mixed and
placed in patches  or overlays by the  city of
Rolla, Missouri. Observation during this phase
may suggest modifications in  the normal plac-
ing and  compacting procedures that  would
facilitate  placing  the bituminous-glass  mix-
ture. Various tests will be conducted to com-
pare the glass-containing asphalt with other
types of  asphalt mixtures.

FINDINGS:  Bituminous  mixtures  satisfying
Marshall design criteria recommended by the
Asphalt  Institute can  be designed  by  use
of penetration-grade asphalts  and aggregates
composed entirely of crushed glass.
  Although  some  degradation  of the  glass
aggregate does occur under  laboratory  mix-
ing,  compacting, and testing conditions, it is
not considered to be severe enough to affect
pavement performance.
  Severe stripping occurs when a bituminous
concrete using dense graded glass aggregates
and asphalt cement is subjected to a standard
laboratory water immersion  procedure. By
the  addition  of commercial antistripping
agents,  this stripping is appreciably reduced.
               Using Wastes Formed in Vegetable and Cheese Production
                        Dr. Amihud Kramer
                 Department  of  Horticulture
                    University of Maryland
            College  Park,  Maryland  20742
  Grant No. EC 00256-03
  Funds Awarded: $142,126
  Project Period: Jan. 1,  1967 to June 30,  1970
OBJECTIVES:   To  study  the  chemical, nutri-
tional,  and  microbiological  composition  of
waste materials occurring during the manu-
facture  of processed fruits, cheeses, and vege-
tables. To  investigate the possibility of using
these waste products as food  or feed for man,
farm animals, plants, or soils.

APPROACH:   During the  first  year  of  the
study,  the  composition  of  various  tomato
wastes was determined  in the fresh stage as
well as  in  various  stages of  silage fermenta-
tion alone, under varying  moisture  condi-
tions, and  mixed  with  an equal  amount  of
corn cobs.  Ensiling consisted of placing  the
material in  a heavy-duty polyethylene bag
and sealing  the  bag to  promote  anaerobic
fermentation. At  various  times during  the
ensiling process samples were  analyzed  for
nitrate,  phosphorus, potassium, calcium, mag-
nesium, copper, zinc, and manganese content.
The presence of selected vitamins and organic
acids was also determined. During the second
year,  various  tomato wastes  were  placed  in
10-ft-high by 6-ft-diameter silos,  and after ap-
propriate ensiling times, feeding studies were
conducted on sheep to determine the poten-
tial  of feeding tomato wastes  to  ruminants.
When problems  were encountered  with  the
palatability of tomato waste products, studies
were conducted to determine the effect of mix-
ing tomato wastes with other plant  materials
to make them  more  palatable  to  ruminants.
  During the second and third years of  the
study fresh, fermented, dried, and fermented-
dried wastes were also fed to poultry. The
fresh wastes were also applied to  different
soil types. Depending on the analytical-chemi-
cal  determinations,  nutrients  or  other sub-
stances found in  quantity were extracted by
various methods.
  Cottage  cheese  and cheddar cheese wheys
were studied, and their applicability as human
foods was determined. The wheys were con-
centrated to various solids concentrations by
different drying methods. The concentrated
wheys  were  then evaluated for  nutritional
value,  and  feeding studies  of  selected whey
concentrations were made on chicks  and rats.
  In the second and third years of the study
                                                                                      95

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attempts were made to use wheys collected and
treated  by different methods as components
of new or modified foods.

FINDINGS:   Chemical  analyses  revealed that
tomato  wastes,  although high  in moisture,
contain a  good  proportion of protein. An
alkaloid, tomatin,  was  found  in  quantities
up to  1/2  percent dry-weight basis in  leaves
to practically zero in  the fully ripe tomatoes.
The vines and stems were also high, par-
ticularly in SiC>2 with  a protein content of
12  to 16 percent dry-weight basis. The ripe
fruit  waste,  on  the  other  hand,  contained
practically  no SiO2 and had 20  to 22 percent
protein dry-weight basis.
  Feeding  studies with  ruminants indicated
that ensiled  vines  and stems are acceptable
to  sheep  provided they are compressed  so
that anaerobic lactic fermentation develops.
Corn cobs  and molasses made the silage even
more palatable.  There  was little  problem
with  feeding ripe fruit wastes  directly  to
sheep. The value of these wastes as feed was
proportional  to their protein content,  being
better than corn but not equal to alfalfa.
  Dried tomato waste could be fed to poultry
up to  25  percent of their  total feed intake
without reducing egg production. When green
tomato wastes were fed at higher levels there
was a decrease in the cholesterol level of the
egg yolk.   At this  level,  however, total egg
production was decreased.
  A process for totally using tomato cannery
waste was  developed  whereby the waste was
compressed,  and  the  pr'esscake  containing
two-thirds  of the solids, 10  percent  protein,
could be  used as  cattle feed,  and one-third
of the solids, 60  percent  protein,  was pre-
cipitated  as  a tomato protein  concentrate.
This concentrate can  be extracted with ace-
tone to form an 85 percent protein isolate
plus a tomato flavor  and  pigment  residue.
This tomato protein concentrate has unusu-
ally good  functional properties and a protein
efficiency  ratio superior to  that  of soy.
  Application of the wastes to soils indicated
that ripe tomato fruit waste  had a temporary
phytotoxic effect. Green tomato waste could
be  added  directly  with little or no phyto-
toxicity.
  The cheese  wheys  contain  approximately
1 percent  protein,  and this causes problems
when the  whey is used as a component or an
ingredient in processed foods.  It was found
that the protein of  the whey could be stabi-
lized by high-temperature, short-time heating.
Whey  thus prepared  could  be used success-
fully as a  milk replacement at levels  of 25 to
50  percent in the  manufacture  of  sherbet,
ice cream, or pudding. It may be mixed with
tomato or other fruit juices as a "fully nutri-
tious  drink."  When it was fermented  with
the appropriate  microorganisms, acceptable
vinegar, beer, and wine were produced.

               PUBLICATIONS

BEN-GERA, I., and A. KRAMER. The utilization of food
industries wastes. Advances  in Food Research, 17:77-152,
1969.
                               Utilization  of Bark Waste
                   Prof. Raymond A. Currier
                 Forest  Research Laboratory
                    Oregon State University
                  Corvallis,  Oregon  97331
 Grant  No.  EC 00276-02
 Funds  Awarded: $132,906
 Project Period: June  1, 1968 to May 31, 1971
OBJECTIVES:   To  implement a  program  in
which chemical and physical sciences are co-
ordinated to promote  economic use of waste
bark  and thus decrease environmental pollu-
tion  caused  by  present  practices.  The  for-
mation of pellets from waste bark was studied
as a  model  system  for  the  preparation of
other molded products such as particle boards
96

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and cups. To obtain a detailed chemical de-
scription  of bark  for carbohydrates,  poly-
phenolic  polymers,   phlobaphenes,  tannins,
and "bark lignin."

APPROACH:   The preparation of pellets from
bark was investigated in a series of experi-
ments  controlling species  of  bark,  moisture
content,  particle size,  and  hardness  of pellet
formation. Information obtained from pellet-
ing bark was used to  prepare molded or ex-
truded products from bark or bark  and  plas-
tics combined. Samples of waste bark in  vari-
ous comminuted  forms were  prepared for
experimental use by companies in the forest
products, adhesives,  or plastics field, or other
public agencies.
  Chemical  composition was  determined on
natural bark, bark that had been ammoniated
to contain 4 percent nitrogen, and bark that
had been broken down into smaller particles
and molded into pellets. By means of column,
thin layer, and gas  chromatography, natural
bark  was analyzed  for  wax,  low-molecular-
weight phenolics, and polymeric phenolics in
"extractive-free"  bark groups.  The  "extrac-
tive-free" bark groups are obtained by se-
quentially extracting bark with hexane,  ben-
zene, ethyl ether, ethyl alcohol, and hot water.
An attempt was made to  isolate and char-
acterize  lignin and  cellulose  fractions  from
the  "extractive-free"  bark group.  Conven-
tional methods were used to characterize new
compounds  and polymers  where possible.

FINDINGS:  Physical  utilization.
  1. Pelleting trials  have been conducted on
15 different  species  of bark,  or mixtures  of
bark  and woody  residues. Other  variables
have  included bark  moisture content,  bark
particle  size, pellet  diameter, and degree  of
pellet densification.  Most species of  bark pel-
let easily, but significant problems have  been
discovered with a  few species. The  densifica-
tion factor during pelleting is 2.5 to 3.0; this
offers a  practical  application  in  transporting
bark wastes.
  2. Molding of bark has  been investigated
in several ways:  (a) Planter blocks  compres-
sion molded or extruded from bark contain-
ing fertilizer and  fungicides  were used  to
grow  tomatoes and  pansies from seed, and
then the blocks plus plants were field planted
with  success,  (b} Another investigation in-
volved  a three-way cooperative study  with
industry.  The Forest  Research Laboratory
prepared dry comminuted bark, and a lumber
company provided the raw bark and financed
experimental time on molding machines at a
plastics producer. Several  types of extruded,
sheet-formed,  and injection-molded products
have  been produced, with bark extension of
the plastic of about 40 to 60  percent. Pre-
liminary economic analyses appear  favorably
inclined toward  commercial application,  (c)
Douglas fir bark has been prepared for a com-
pany  interested  in  extrusion of a  fuel log.
Trial  runs  have indicated a log containing
largely bark can  be  formed by this particular
process.
   3. Samples  of  bark  or bark fractions have
been  prepared  for  several companies  inter-
ested in potential use of bark in  their  prod-
ucts.  In particular,  one concern is interested
in chemically extracted bark as an extender
for wood  adhesives. A cooperative project
with  the Agricultural  Engineering Depart-
ment  of Oregon  State University has  re-
sulted in exploratory research on use of bark
in a  trickling filter system  for disposal  of
animal wastes.
   Chemical  utilization.  The  chemical  in-
vestigation of bark has involved the areas of:
(1) hexane solubles, (2) benzene solubles,  (3)
bark carbohydrates, and (4) ammoniated bark.
   The hexane- and benzene-soluble fractions
are mostly of the "vegetable wax"  type, and
the research has concerned the chemical com-
position of these waxes. The bark carbohy-
drate  studies  have  involved isolation  proce-
dures. The separation  has resulted in frac-
tions  containing the polyphenolic  polymers,
the phlobaphenes,  the  tannins, the bark lig-
nins,  and finally the insoluble carbohydrates.
   The "ammoniated bark" has been prepared
by treatment of natural bark  with gaseous
ammonia to a nitrogen content of about 4
percent. For comparison purposes the experi-
mental procedure  on  this treated  bark has
been  similar to  that on "natural bark."
   1. Hexane-soluble wax fraction,  (a) Analy-
ses by spectral methods have  indicated that
this  wax contains  two long-chain fatty  al-
cohols that  may  be  behenyl (€22) and  ligno-
                                                                                       97

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ceryl  (C^) esters of ferulic acid. Gas chroma-
tographic methods have been developed  to
separate these alcohols for analytical purposes.
(b)  Column  chromatographic separation  of
the whole  hexane wax shows  two bright yel-
low-green  bands  that are  incompletely re-
solved. After elution  from the column, these
bands have been  shown by thin-layer chro-
matography to contain at least 10 components.
The main fraction from the  thin-layer  sepa-
ration has been further resolved into three
components  by  gas-liquid chromatography.
The  major fraction from  the gas chromato-
gram was  collected and its structure deter-
mined by  infrared, ultraviolet, and nuclear
magnetic resonance spectroscopy. (c) Quali-
tative analyses of the alcohol fraction  (neutral
fraction) and the  acid fraction of the hexane
wax were made by gas-liquid chromatography.
  2.  Benzene-soluble  wax  fraction. Separa-
tion of two compounds that appear  as yellow
bands on column  chromatographic separation
of the entire benzene wax has been accom-
plished.  These  compounds are highly  (and
pleasantly) aromatic.  Resolution of  this mix-
ture  into  their pure compounds  is under
investigation by  both thin-layer  chromatog-
raphy and gas-liquid chromatography.
  3. Bark  carbohydrates,  (a)  The inner bark
was collected from a standing Douglas-fir tree
 135 years  old.   (b) The inner bark  was suc-
cessively   extracted   with   80/20:: ethanol/
water, 2/1: :benzene/ethanol,  hot  water,  di-
lute ammonium oxalate, and acidified sodium
chlorite,  (c)  The 80/20: :ethanol/water ex
tract  (15.4 percent of the inner bark) con-
tained a trace  of free glucose, as shown  by
paper chromatography.   (d)  The  2/l::ben-
zene/ethanol  extract (3.0  percent of the
inner bark) contained no free sugars, as tested
by paper chromatography.  (e) The  water ex-
tract  (8.6 percent of the  inner bark) con-
 tained a trace  of free glucose, as shown  by
paper chromatography.  Preliminary experi-
ments after acid  hydrolysis  showed glucose
and several amino acids. Color tests also  in-
dicated the presence of starch in this fraction.
(/)  The  ammonium oxalate extract  (3.8 per-
cent  of  the inner bark) contained no free
sugars. After acid hydrolysis the fraction was
shown to contain  glucose,  arabinose, and
trace amounts of  other sugars, (g)  The  holo-
cellulose  (46.2  percent  of the inner  bark)
resulting from delignification  with acidified
sodium chlorite represented the major part
of the carbohydrates of inner bark. Acid hy-
drolysis and paper  chromatography showed
glucose,  mannose,  galactose,  arabinose, and
xylose. Elemental tests showed no nitrogen,
phosphorus, sulfur, or halogens.
  Future  research  on the carbohydrates  of
Douglas-fir bark will be  centered on this im-
portant fraction that makes up 40  to 50 per-
cent  of the inner bark.  The  holocellulose
will be separated into  its component polysac-
charides, and  their structures and  properties
will be determined.
  This investigation will  allow a  close com-
parison between the carbohydrates in  Doug-
las-fir bark  and those  utilized commercially.
Since the inner bark is composed of more than
50  percent carbohydrates  (water extract, am-
monium oxalate extract, holocellulose), it  is
conceivable that a commercially  useful car-
bohydrate will be isolated.
  4.  Ammoniated  bark,   (a)  Untreated-bark
characterization. A large sample of Douglas-
fir  bark  was collected and ground to  a size
suitable for research investigation. The bark
sample had an overall  nitrogen   content of
0.46  percent nitrogen. The bark  was  succes-
sively extracted with hexane  (4.6 percent
solubilized), benzene  (2.70  percent   solubi-
lized), ether  (1.81  percent solubilized),  95
percent  ethanol  (6.38  percent  solubilized),
and hot water (2.20 percent solubilized).  (b)
A sample of this bark was treated with gase-
ous  ammonia  under  laboratory-controlled
conditions of temperature, moisture content,
flow  rate,  and  pressure. The nitrogen con-
tent  of  the treated bark was  4.08 percent.
The  treated bark  was successively extracted
with hexane  (4.63 percent solubilized), ben-
zene  (2.95  percent solubilized), ether (2.21
percent solubilized), 95 percent ethanol (7.13
percent  solubilized),  and hot water   (7.60
percent  solubilized).  (c) A  sample   of the
original  untreated bark  was  ground to pass
a 32-mesh  screen.  The  ground  bark  was
treated with gaseous ammonia as in "b." The
nitrogen  content  was   2.34  percent. The
treated bark was successively extracted with
hexane  (4.16  percent solubilized),  benzene
(3.92 percent  solubilized), ether  (1.19 per-
 98

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cent solubilized), 95  percent ethanol  (6.06
percent solubilized), hot water  (7.00  percent
solubilized) . (d) Detailed chemical analysis of
the bark and the bark fractions is in progress.
               PUBLICATIONS
LEHMANN, W.  F. Molding compounds from Douglas-fir
bark. Forest  Products Journal, 18(12):47-53, Dec. 1968.
                       Utilization of Broiler Litter as Animal Feed
                     Dr.  Joseph P.  Fontenot
               Department of Animal Science
                Virginia Polytechnic Institute
                Blacksburg, Virginia  24061
 Grant  No.  EC 00034-02
 Funds Awarded: $68,668
 Project Period: June  1, 1968 to May 31, 1971
OBJECTIVES:   To  develop a satisfactory steri-
lization  method  to  destroy pathogenic  or-
ganisms  in poultry litter  and thus  convert
the litter  into  a  useful product as animal
feed.  The  sterilized litter is being  tested for
nutritive value, palatability, and possible toxi-
cologic effects. The cattle and sheep used for
the feedings are being tested for organoleptic
qualities,  wholesomeness of meat, and  possi-
ble take-up of drug or pesticide residues.

APPROACH:   Different litter sterilization tech-
niques are being examined,  such  as  auto-
claving at 116  C under steam pressure  for
30 to 120 min, heating in a forced-draft oven
at 100 and 150  C for 4 to  48  hr, fumigating
with ethylene oxide, sterilizing with beta pro-
piolactone from periods  of  30 min to 24  hr
and, finally, piling in  deep stacks  for  30  to
120 days to encourage normal heating of the
litter. Anaerobic organisms are being counted
by  use of  PRAS  media. Approximately 150
samples are being used to check  for sterility.
Litter from sterilization  methods proving  to
be  successful  are  being  analyzed for proxi-
mate components, true  protein, uric acid, Ca,
P, NH3, drugs, and  pesticides.
  Litter is secured from various producing
areas  to ensure  that  representative  samples
are being obtained. Short- and  long-term feed-
ing experiments  are  being carried  out  to
determine  if  toxic factors  are present. For
the short-term  experiment, castrated  male
sheep  are  fed rations  containing 0,  25,  50,
and 75 percent sterilized litter for 80 days.
The test animals are checked daily for water
intake and  urine  volume, and urine is  ana-
lyzed for protein, sugar, ketone bodies, biliru-
bin, crystals, occult blood, and specific gravity.
Blood is  analyzed for urea and NH3,  total
red  and white  cell counts, and differential
white  cell  count. Rectal  temperatures  are
recorded  daily.  At the end of the  feeding
period, the sheep are sacrificed,  and a  de-
tailed necropsy is  made, including the prepa-
ration of histologic sections of  the kidneys.
For long-term studies,  breeding ewes are used.
They are fed  dry-lot for 3 years; control and
experimental  diets contain 25 and  50 percent
replacement. The ewes are bred once a  year
and are frequently examined as in the short-
term experiments.
  Nitrogen utilization and energy values are
determined. The palatability of the litter for
cattle  and  sheep  when  feedings   are on  a
free-choice basis is being observed.  One group
of cattle  and one group  of sheep are used
for   meat evaluation  trials  such  as carcass
conformation  scores, maturity, marbling, final
grade, and organoleptic quality.   All  trials
are  analyzed by accepted statistical  procedure.

FINDINGS:   It  has  been found  that  heating
broiler litter in a forced-draft  oven at 150 C
for  4 hr or longer is effective  in  sterilizing
the litter. None of the other procedures have
been effective.
  Autoclaving or  treatment with chemical
sterilizing agents has had no consistent effect
on  chemical composition  of the litter. The
                                                                                         99

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use of dry heat at  100 or 150 C  for 4 to 48
hr resulted in about a 20 percent loss in crude
protein. The protein level of the sterile prod-
uct is still, however, very high, about 32 per-
cent,  dry  basis, which  compares  favorably
with  the  protein  level of many  commercial
protein supplements for livestock. The pH of
unprocessed  litter was  found  to be  about 8.
Acidifying the litter prior to dry heat process-
ing by the addition of  dilute hydrochloric or
sulfuric acid to a pH of about 6 resulted in
a nitrogen loss of only about 8 percent.
  Considerable  variation in  chemical  com-
position of samples has been  obtained from
different areas of Virginia, especially for crude
protein, ash and  gross energy, but all sam-
ples  have  contained  substantial   nutrient
levels. This variation in nutrient  level would
not preclude  the use of poultry litter as ani-
mal feed,  since certain  other feedstuffs on
the market also show considerable  variation.
  The only pesticide residues  detected in the
poultry litter have been low  levels  of DDT
and its breakdown products. Since DDT had
not been used  in any of the broiler houses
from  which  the samples were obtained,  the
residues probably  originated  from  the  feed
supplied the  birds.
  In  the 80-day feeding experiment, in which
sheep were  fed diets  containing up to  75
percent sterilized broiler litter, no gross toxi-
cologic effects were observed. There were no
feed refusals when the  ration  contained up
to 25 percent  litter.  Feed intakes were de-
pressed  at the  higher litter levels, especially
when the ration contained 75  percent litter.
Feeding  litter had no  consistent effect on
various  physiologic parameters  such as rectal
temperature;  water  intake;  urine  volume;
blood ammonia, blood urea, total red blood
cell numbers, and total and differential white
blood cells; and  urinary pH, specific gravity,
glucose,  ketones, bilirubin,  protein,  and oc-
cult blood. At slaughter none  of the organs
showed  any gross  abnormalities. Studies of
histologic  sections  of  brain,  lungs,  liver,
spleen,  and kidney  indicated that  feeding
high levels of  sterile  litter for as long  as 80
days did  hot produce any pathologic effects.
   In  the long-term experiment  with breed-
ing ewes, thus far, feeding up to 50 percent
sterile litter has not produced any deleterious
effects.  Lambing of  the  ewes is essentially
complete and, at this point, it does not appear
that litter feeding has affected performance.
                PUBLICATIONS

FONTENOT, J. P., R. E. TUCKER, B. W. HARMON,  K. G.
LIBKE, and W.  E. C. MOORE. Effects of feeding different
levels o£ broiler litter to sheep. Journal of Animal Science,
30:319, 1970. (Abstract.)
                  Utilization of Fibrous Wastes as  Sources of  Nutrients
                  Dr. James M. Leatherwood
              Department of Animal Sciences
              North  Carolina State University
             Raleigh, North Carolina  27607
  Grant No. EC 00274-03
  Funds Awarded: $80,555
  Project Period: Feb.  1, 1968 to Jan. 31, 1972
OBJECTIVES:   To develop a  biologic tech-
nique for the conversion of natural cellulosic
wastes to  products  that can  be  utilized as
nutrients by animals. Particular emphasis is
given to the optimization of biologic systems
that can effectively  degrade cellulosic wastes
and to  the  evaluation  of the  degradation
products as a source of animal  feed.
APPROACH:   Anaerobic bacteria  are used as
hydrolytic agents in batch-, semicontinuous-,
and continuous-fermenter systems employing
initially either cotton linters  or newspaper
as  substrates.  The  products  from the  fer-
menters,  which  include  volatile fatty acids,
soluble carbohydrates, residue, bacterial cells,
 100

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and  protein, are evaluated 'as  nutrients for
animals.
  Cellulose-utilizing  bacteria  are  isolated
from natural habitats of sewage, rumen,  and
soil and  from cellulose enrichment cultures.
The effects  of  pH,  temperature,  substrate
composition  and  concentration,  and  other
environmental  factors on  the effective  level
of cellulolytic activity  are  determined. The
effects  of various agents on the synthesis and
activity  of  the  cellulose-degrading  enzymes
produced by the bacteria are being investi-
gated.  The development of mutants by means
of chemical  mutagens  is being investigated
as a method  of increasing  the effectiveness
of the bacteria.
  Apparently, there are controls within the
biologic  systems that alter the rate and ex-
tent of cellulose utilization. A  better under-
standing of  the biochemical  mechanism of
cellulose hydrolysis will allow more effective
application  in the fermenter system. These
controls  and mechanisms  are being investi-
gated.  The co-inoculation  of methanogenic
and proteolytic  bacteria along with the cellu-
lolytic bacteria is being tried as a means of in-
creasing  the efficiency and rate of degradation.
  The nutritional evaluation  of the end prod-
ucts of fermentation is  based  on the response
of animals to diets containing such products.
Rats are used  as  the  test animals  in initial
studies. Diets containing the concentrated cul-
ture effluents from the fermentation process
are compared with diets  containing the un-
treated cellulosic  material  and with a  posi-
tive control  diet containing  a carbohydrate
known to  be utilized  well by the rat. The
nutritive biologic value of  the  bacterial  pro-
tein that is  synthesized from  inorganic nitro-
gen is being evaluated in similar feeding trials
with rats. When sufficient progress has  been
made to  permit operations on a larger scale,
the end  products will  be fed to either sheep
or swine in feeding trials.
FINDINGS:  Several  cellulolytic   strains  of
Bulyrivihrio fibrisolvens,  Ruminococcus  al-
bus, and R. flavcfacieiis  were isolated  from
the bovine  rumen.  Two of the new strains
ol R. jltivcfaf iens were compared with known
strains isolated by other investigators at Belts-
ville,  Maryland,  and Ohio State  University.
There were no significant differences in the
ability of the  bacteria to degrade  cellulose.
There was  some  similarity  among  the par-
tially  purified  hydrolytic enzymes on an im-
munochemical basis.
  Cellulolytic  enzyme  synthesis  in  several
strains of R.  flavejaciens  and R.  albus was
repressed  by  moderate  levels of cellobiose,
as shown  by  the  decrease in  clear-zone for-
mation on  cellulose-agar  roll tubes.  These
experiments demonstrated a  natural control
on enzyme  production and therefore a limit
on the rate of cellulose degradation.  There
was no inhibition of the hydrolytic enzyme
by cellobiose. Attempts  to eliminate this re-
pression by  means of chemical mutation have
not succeeded. Further studies along this line
are, however, in process since this  is one of
the standard  techniques used in  industrial
microbiology  to improve efficiency and yield.
  An  apparent  protein-protein  interaction
has been  observed  in cultures  of  Rumino-
coccus that results  in the formation of an
enzyme complex that degrades cellulose. Two
different  components diffuse  from  different
colony  types  on cellulose-agar roll  tubes to
form  a single enzyme complex that degrades
cellulose.  A new mechanism  for cellulose deg-
radation  has  been  postulated that is based
on the combination of an affinity factor and
a hydrolytic factor to form a complete cellu-
lase  that  can  hydrolyze native  cellulose to
cellobiose. The previously held hypothesis on
the mechanism of cellulose degradation  re-
quired two  separate enzymes for  the degrada-
tion of native cellulose. This new mechanism
has been considered in relation to the general
phenomena of resistance, extent,  and nature
of cellulose  hydrolysis. Experiments  are being
conducted to  elucidate  this  new  mechanism
further.
  Small  fermenters  (700-ml  Kelly  infusion
bottles) were  used  to  study  parameters of
fermenter operation. Cotton linters were used
as substrate and Ruminococcus albus  was
used  as the  hydrolytic  agent  in  a  semicon-
tinuous operation with  a cycle every 3 to 5
days.  Fermenter effluents  were analyzed for
volatile tatty acids, bacterial protein, soluble
                                                                                       101

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carbohydrates, and total organic matter.  Gas
analysis from the fermenter showed consider-
able hydrogen production. Methanogenic  bac-
teria were  added  to  the system to remove
the hydrogen, a possible  inhibitor.
               PUBLICATIONS
LEATHERWOOD, J. M. Cellulase complex of Ruminococcus
and a new mechanism for cellulose degradation. In Cel-
lulases  and their  applications.  Washington, American
Chemical Society,  1969.  (Advances in  Chemistry Series,
95). p. 53-59.
                  Wood  Waste Reuse  in  Controlled-Release Pesticides
                      Dr. G. Graham Allan
                 College of Forest Resources
                   University of Washington
                Seattle, Washington   98105
 Grant No. EC 00319-01
 Funds Awarded: $37,437
 Project Period: June  1, 1969 to May 31, 1972
OBJECTIVES:   To enhance the effectiveness of
pesticides by chemically bonding certain pes-
ticides to solid waste so that the pesticide  is
released  slowly over a long period of time by
breakdown  of the  pesticide-solid waste com-
bination.  Pulping  wastes  and screenings,
lignin, sawdust, and solid wood waste such
as bark  are used as  the  substrates  to  which
the pesticides  are chemically bonded and thus
an inactive solid waste-pesticide combination
is afforded.

APPROACH:   A few representative pesticides,
such   as   2,4-dichlorophenoxyacetic   acid
(2,4-D);  at  2,4,5-trichlorophenoxyacetic acid
(2,4,5-T);  and 2,4,5-trichlorophenoxybutyric
acid (2,4,5-TB),  contain a functional  group
that possesses a replaceable hydrogen.  A hy-
drolyzable ester-type linkage could be formed
between  the hydroxyl group in the wood waste
and  the carboxyl group in the  pesticide. Re-
lease of  the pesticide  from the solid waste-
pesticide combination is being studied in soil
under laboratory and field conditions.
FINDINGS:  Several methods  for  the attach-
ment  of carboxyl-containing  pesticides  to
wood wastes are being studied and compared.
A number of pesticide-solid  waste combina-
tions have been prepared  in amounts suffi-
cient for testing and  analyzed for their  pesti-
cide  content.  Greenhouse  experiments  to
assess the ability of these combinations to con-
trol deciduous  growth in the presence  of
conifer seedlings are  now underway. Another
preliminary series of tests designed to measure
the durability of  these solid  waste combina-
tions in preventing the germination of weed
seeds has also been initiated.
                   Solid Waste  Disposal and Bird Hazard to Aircraft
                     Dr. Howard L. Cogswell
            Department of Biological Science
          California State  College, Hayward
                Hayward,  California   94542
 Grant No. EC 00277-02
 Funds Awarded: $77,427
 Project Period: June  1, 1968 to May 31, 1971
 OBJECTIVES:   To study the factors emanating
 from solid waste disposal by various landfill
methods that have significant influence on
the kind, the degree,  and the daily and sea-
 102

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 sonal  timing of hazard .to  aircraft through
 collision with birds.  To survey bird popula-
 tions and movements for 1 year at most of the
 disposal sites and airports about San Francisco
 Bay, with particular attention to flight routes
 to  and from the  disposal sites near  major
 airports. An intensive analysis is being made
 of the number  of  birds and their regularity
 of  travel between  major  disposal sites  on
 opposite sides of the bay and on either  side
 of particular airports.  A less intensive com-
 parison is being made near  airports  on the
 rest of the West Coast, and  on the  Gulf and
 Atlantic Coasts, in order to  evaluate applica-
 bility  of  the findings  in  the San  Francisco
 Bay area.

 APPROACH:   From September 1968 through
 April 1969, semimonthly surveys of bird popu-
 lations were made  at the major disposal sites
 and at all airports  around San Francisco  Bay
 proper and  less frequently  at such disposal
 site-airport combinations as are available near
 San  Pablo  and  Suisun Bays. Monthly  sur-
 veys  were  then made  from May  through
 August 1969 at all  the disposal  sites  and
 airports, and this schedule of population es-
 timates is  being largely continued in 1970.
 Counts are  made by  observers in ground ve-
 hicles  and by a small airplane;  this permits
 coverage of areas not accessible  by car,  and
 rapid  inventory  of large areas.  Populations
 thus surveyed include  all birds  attracted to
 the disposal sites that could potentially  fly
 through the danger zone near airports going
 to and from dumps,  but most  attention  is
 given  to  gulls,  which  constitute the  major
 hazard near salt water. Maps of the  whole
 bay area at the scales of 1:24,000 and 1:62,500
 showing detailed habitat features and loca-
 tion numerals are  used for  noting  the posi-
 tion and numbers  of birds and  for showing
 flight routes.
  During the seasons when bird populations
 reach a high level,  several hundred gulls are
 captured at selected disposal sites and marked
with plastic back tags for subsequent identi-
fication.  A  few  are  marked  and  relocated
with small radio telemetry devices.
  As  the  pattern of bird movements  to and
 from  disposal sites and airports in the San
Francisco  Bay region becomes apparent,  the
principal investigator is expanding the study
by comparing bird habitats and movements
at other disposal sites and major airports else-
where in the country, particularly near the
coasts.

FINDINGS:  In the  San Francisco Bay region,
where the intensive  field work of this study
is concentrated, there were  in  1968 and 1969
a  total of 7  major  airports  (4 military,  3
civil) and  13  smaller airfields  located within
5 miles of the bay  shore or its tributary tidal
channels. In the same belt of mostly low-lying
lands about the bay there were 37 solid waste
disposal  sites,  31 of which were found to at-
tract  birds in considerable  numbers.
   From  five  to seven species of  gulls  are
attracted  regularly  to  disposal  sites  in  this
region. Of all factors  associated  with  the
disposal  operations,  the daily  cycle  of gull
movements creates  by far the greatest hazard
to  the safety  of aircraft  operations  at  the
nearby airports. Starlings, blackbirds  of four
species, and in some locations, crows, ravens,
and occasional  herons, vultures,  or hawks
constitute  the remaining  species  using  dis-
posal sites that also  contribute  to  the bird-
strike  problem  because of  their size  and/or
habit of long distance flights,- or both.
  When on a disposal  site,  gulls feed almost
entirely in the  freshly deposited refuse con-
taining significant  amounts  of garbage, par-
ticularly closely around the bulldozers. Most
of these  gulls do not feed elsewhere than at
the refuse, and so it is thought that the food
supplied by garbage  is a significant factor in
supporting the large populations of fall, win-
ter, and spring.
  From combined ground and aerial observa-
tions, total numbers of gulls in the  vicinity of
the bay south of the  San Francisco and Oak-
land-Alameda  harbor areas  were  computed
at about  80,000 in  October and  85,000  in
mid-December 1968. Only 53,000 were located
in January, 55,000 in March, and these figures
dwindled to 16,000 by May and 3,600 at the
low point  in  June  1969 (more than  half of
these  being in one  unit at the southeast end
of the bay).  Early  returnees from  breeding
grounds  had  increased the total population
again to 25,000 by  late July.
  In  the  north bay, censuses  of gull popu-
                                                                                      103

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lations were  less nearly  complete,  but fairly
thorough air counts showed 30,000 to 34,000
from early  October to  mid-February,  total
numbers  declining  to  6,300  by  late April,
4,300 by late  May, and  to less than 2,000 in
mid-June.
  Peak numbers arrived at the core area in
various seasons  close to  7:30  a.m., at which
time bulldozing of refuse was beginning. De-
parture,  hoxvever, took  place within  about
1 to 2 hours before sunset, or in accordance
with diminishing light, even though  disposal
operations had ceased  long  before. These
flights to roosting and  feeding areas would
present  a  significant hazard  to   aircraft  if
they were  across an airport or its approach
and takeoff corridors.
  The  gull  population  unit north  of the
Hayward area contains three disposal  sites,
two of them  accommodating a high volume
of garbage daily. The Metropolitan Oakland
International  Airport lies between these two
sites, some of the  core area activities of gulls
taking place  within  its boundaries. On roost-
ward  flights   from  the  Davis St.  site  large
numbers of gulls  travel  nearly due westward
(usually  at 100  to  300 feet  high)  directly
across the jet runway 11-29  or its southeast
approach. These gulls apparently go to roosts
in  the middle of  or on  the western  shore of
the bay,  but tracing  them to their destinations
has  not yet  been  possible.  At the  peak of
this flight in  November  1969, about 4,000
gulls flew within 10 minutes through the air-
space normally used by jet aircraft in the last
mile of final approach  to landing  (1 mile
from the disposal site). Although this mass
exodus is  rather  unusual, gulls  arriving at
this core area in  the  early morning and de-
parting  in the  afternoon  commonly showed
densities of 150 to  500  birds per  1,000 ft of
flight  "front"  per  10 minutes,  at distances
of  1  to  2 miles from the disposal site. Peak
hazard times for aircraft close to ground level
at  Oakland  thus  coincide with  these  flights
of gulls  to and from roosts.
   In the entire region, gulls fly from one
disposal  site  to another  and to distant reser-
voirs.  On such "commutes"  large numbers
pass  through air traffic  patterns  at Moffett
and Alameda Naval Air Stations,  Palo Alto,
Oakland, Fremont,  and Skysailing Airports,
and  at  Travis  Air .Force. Base. Numbers of
gulls  noted on  our visits to  other  airports
were  much lower.
  The marking and  subsequent recognition
of individual gulls have as shown that there
is much more shifting from one disposal site
to another than was expected from the rather
stable numbers present.
  This  considerable fluctuation of  member-
ship in  a  particular population adds further
complication to the problem of altering solid
waste disposal methods or locations  so as to
reduce bird-strike hazards to aircraft. Merely
improving one dump, or controlling the birds
at it  by various  alarm,  repellent,  or poison
methods will be  no more than a temporary
aid.  When food is again available  and the
flocks resting in a core  area  are  not often
disturbed,  a  population buildup  through
"around the bay" wanderers would take place.
Indications are,  therefore, that  it  will  be
necessary  to institute region-wide  improve-
ment in solid waste techniques or to carry out
intensive  and expensive repellent or control
methods  indefinitely.
   In June and September 1969 the principal
investigator visited major and medium-sized
air terminals on  and near the Atlantic coast
from Portland, Maine, to Norfolk, Virginia.
Discussions with airport staff,  and in many
cases visits to  nearby  disposal sites, led to
better understanding of the possible influence
of solid  waste disposal  operations  on bird
presence and movements at the airports. The
following three areas bore remarkable resem-
blance to the situation in the  bay region of
California:  Boston, New York, and  Norfolk.
In each of these  cases, the airports are on or
close to bays or tidal marshes—natural high-
ways for  gulls—and  there  are disposal sites
handling  large volumes of garbage and rub-
bish  within a  few miles. Different  jurisdic-
tions are  also involved in the seeming inabil-
ity to plan for correcting the situation. At the
Logan International  Airport,  Boston, and at
Kennedy, La Guardia, and Newark Airports,
operated  by the Port of New York Authority,
the airport management is both aware  of the
problem  and attempting to  discourage birds
that constitute hazards.  The  nearby disposal
sites, documented as the focal  points of gull
activity in the region, are not, however, under
 104

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their control. The indicated ultimate solution
in these  areas,  and even more so in the San
Francisco Bay  area  with its  9  counties  and
more than 50 cities,  is regional control of the
solid wastes operation.
               PUBLICATIONS
COGSWELL, H. L. Gulls and solid waste disposal in the San
Francisco Bay area,  California.  In  Proceedings;  World
Conference on Bird Hazards to Aircraft, Queen's Univer-
sity, Kingston, Ontario, Sept. 2-5, 1969. [Ottawa], National
Research Council of Canada,  [1970].
               Microbiology  and  Acid  Production  in Sanitary Landfills
                 Professor Jerry C. Burchinal
            Department  of Civil  Engineering
                   West Virginia University
         Morgantown, West Virginia   26506
 Grant No. EC  00249-03
 Funds Awarded: $77,029
 Project Period: Jan. 1, 1967 to Dec. 31, 1969
OBJECTIVES:  To determine how decomposi-
tion in sanitary landfills  may be speeded or
slowed through the judicious use of nitrogen,
phosphorus,  and  potassium,  under varying
conditions  of  moisture,  temperature,  and
compaction.  To determine the  succession ot
microorganisms during the decomposition of
municipal refuse,  the order of occurrence of
organic acids and  the  species  of microor-
ganisms responsible for their formation, and
the rate and quantity  of gas produced per
unit of refuse.
tempt was made to determine the substrate
from which  the  organic acids  were formed.
Once the growth of various organisms on  the
various refuse components  had been  deter-
mined, decisions concerning the addition of
potassium,  nitrogen,   and   phosphorus   to
hasten the microbial metabolism were  made.
  The gases  produced in a simulated landfill
were analyzed, and  the effect of different types
of refuse  and moisture content of the  refuse
determined.
APPROACH:   Fresh  household  refuse   was
placed  in  simulated  landfills  consisting of
cylinders ranging in size  from 12 to 36 in.
in diameter and from 4 to 16 ft high. Repre-
sentative samples  of fresh household refuse
were ground and  analzed  for nitrogen, phos-
phorus, and  potassium  by  using  standard
methods of analysis.  The  microorganisms of
a large uniform sample of  fresh household
refuse  were isolated  and identified.  The re-
mainder of the refuse  was then placed  in a
simulated landfill.  To  determine the succes-
sions  of  microorganisms  as  decomposition
proceeded,  subsamples  of  the decomposing
refuse  were taken, microbial isolations  were
made, and  the isolates were identified.
  Organic  acid determinations were made by
using  gas   chromatographic  techniques. A
search  was then  made to  identify  the  or-
ganisms producing the various acids. An at-
FINDINGS:  The  following  fatty  acids  were
produced  in  refuse  decomposition:  acetic,
propionic,  iso-butyric, n-butyric,  iso-valeric,
n-valeric, iso-caproic,  and  n-caproic;  acetic
and  n-butyric  were the most plentiful. Or-
ganisms  likely  to have been responsible in-
clude Clostridia  and  E. Coli, CO2,  N2, and
NH4. Protein yielded larger acid concentra-
tions than carbohydrates or fats  did.  Opti-
mum temperature range for acid production
was  30 to 55 C.  Optimum  moisture  for acid
production was 60  to  80 percent. Better deg-
radation  in refuse  occurs  with  1.86 percent
organic  nitrogen as N, 0.31  percent  phos-
phorus as P and  0.23 percent potassium as K
than at  higher or  lower values.  In  general,
decomposition  of refuse in landfills is related
to the  level of nitrogen, the nature  of nitro-
gen  (organic is better than  inorganic),  mois-
ture, temperature,  and  time.  Bacilli  and
                                                                                       105

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Clostridia appear to  be  the most common
genera in refuse incubated at 25°C and Lacto-
bacilli, bacilli,  and Clostridia at 55°C. Iden-
tified  isolates  of  bacteria,  obtained  from
incubated refuse,  produced  fatty  acids  in
media containing glucose or amino acids as
the sole source of carbon,
                • PUBLICATIONS
DOBSON, A. L., H. A. WILSON, and J. C. BURCHINAL. Fac-
tors influencing decomposition in sanitary landfills. Bac-
teriological Proceedings, A77, 1965.  (Abstract.)
QASIM, S. R., and J. C. BURCHINAL. Leaching of pollutants
from refuse  beds.  Journal of the Sanitary  Engineering
Division, American Society of Civil Engineers, 96(SA1):
49-58, Feb. 1970,
                               Sanitary  Landfill  Investigation
                      Prof. Jerry C. Burchinal
              Department of Civil Engineering
                     West  Virginia  University
          Morgantown, West Virginia  26506
  Grant No. SW 00038-03
  Funds Awarded: $87,337
  Project Period: June 1, 1962 to May 31,  1966
OBJECTIVES:   To  identify  the groups  of mi-
croorganisms active in refuse decomposition.
To study oxidation conditions of buried ref-
use and the effects of moisture,  temperature,
nitrogen,  phosphorus, and potassium on ref-
use  decomposition. To  investigate  gas pro-
duction and its composition. To obtain basic
chemical  and  bacteriologic  data concerning
water pollution emanating from solid waste
landfills.

APPROACH:   To accomplish these objectives,
fresh household refuse and material retrieved
from  landfills were  studied  in parallel.  In
addition,  the  effects  of different strip-mine
spoils on refuse,  either  mixed  or  in  layers,
were  evaluated.  Generally, laboratory  inves-
tigations were done  under controlled condi-
tions, various  test cylinders  being used for
simulated landfills. In  some  cases, sampling
pits were constructed  in  operating landfills at
Morgantown,   along  with  observation  and
sampling wells.

FINDINGS:  Sanitary  landfills  can  seriously
damage underground  water  by  causing  an
appreciable  increase  in hardness,  iron, solids,
and various forms of nitrogen  and  sulfur.
Methods of  limiting gas  penetration into the
aquifer are  desirable. Volatile acids intensify
the  leaching of fill materials. Large popula-
tions  of aerobic  mesophilic  bacteria  were
found  in exterior  seepage from  the landfills.
Coliform bacteria  were  found in both  fresh
household refuse and in  sanitary  landfills.

                 PUBLICATIONS

DOBSON,  A. L., and H.  A. WILSON. Refuse decomposition
in strip-mine  spoils. Proceedings  of the West Virginia
Academy of Science, 35 (Series  64 No. 7-4):59, Jan. 1964.
DOBSON,  A. L., H.  A. WILSON, and J.  C.  BURCHINAL.
Factois  influencing decomposition in sanitary landfills.
Bacteriological  Pioceedings, A77, 1965.  (Abstract.)
COOK, H. A., D. L. CROMVVFLL,  and H. A.  WILSON.  Micro-
organisms in  household refuse and  seepage  water from
sanitary  landfills. Pioceedings of the West Virginia Acad-
emy  of Science, 39:107-114,  1967.
QASIM, S. R., and J. C. BURCHINAL. Leaching of pollutants
from refuse beds. Journal of  the Sanitary Engineering
Division,  American Society of Civil  Engineers, 96(SA1):
49-58, Feb. 1970.
 106

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                         Special  Studies of a  Sanitary Landfill
                       Prof. Robert C.  Merz
            Department of Civil  Engineering
           University of Southern California
            Los Angeles,  California  90007
 Grant No. U1-00518-08
 Funds Awarded: $191,436
 Project Period: Jan. 1,  1960 to  Dec. 31, 1968
OBJECTIVES:   In the  first  3-year period, to
study the effects of physical and chemical phe-
nomena on the decomposition  rate of organic
matter in a landfill and the resulting effect on
volume reduction through  field and labora-
tory efforts. During  the next 2 years, to con-
tinue the initial objectives  and add artificial
rainfall plus aerated,  irrigated, and gas  col-
lection  test  cells.  During   the  final  3-year
period, to continue the previous 5 years' work
to permit long-term  evaluation and  quantita-
tive data collection.

APPROACH:   Test sanitary landfill cells were
constructed  at a Los Angeles County Sanita-
tion  District  disposal  site.  The field tests
considered the influence of moisture, soil  ad-
mixture, depth  of fill,  type  of soil,  aeration,
and temperature on degradation of organic
matter in sanitary landfill and on fill  settle-
ment. At the site, temperature, humidity,  and
gas composition were measured automatically.
The  second project  period continued   the
study of the  first six cells and added four to
investigate the effects  of forced aeration,  ar-
tificial rainfall typical of a  humid area, field
crop irrigation,  and total gas  collection  and
analysis.  The final 3-year period continued
detailed  data collection and evaluation.   To
ensure maximum control of the  study each
load of refuse was weighed  and categorized.

FINDINGS:  During the first  3-year period,  the
following was observed.
   1. Compared  with the landfill  constructed
in the usual anaerobic manner,  which uses
4-ft lifts  separated by  1-ft-thick earth covers,
the initial in-place density of refuse (a)  was
increased by about 20  percent in a  similarly
constructed  landfill  through the addition of
sufficient water  to maintain a moisture con-
tent of approximately 40 percent;  (b) was in-
creased by about 35 percent through the use
of an 18-ft lift, the addition of sufficient water
to maintain saturation, and the providing of
good compaction; (c)  was approximately the
same in the  landfill  built with  continuous
admixture of  earth plus the addition of suffi-
cient water to maintain a moisture content of
approximately 35 percent;  (d) was increased
from about 6  to  35 percent by the particular
and  varied methods of construction used.
  2.  The landfill constructed in an anaerobic
manner with a total depth of 20  ft provided
an initial in-place density from about 5 to 15
percent more  than that obtained at  the 9-ft
depth.
  3.  Normal compaction procedures used in
landfill construction provided initial  in-place
densities of refuse from about 15 to 50 per-
cent  more than the delivered  truck  density,
depending upon  the method of construction
used.
  4.  The landfill constructed  in  an aerobic
manner, by using 18-ft lifts and added water,
maintained an  active composting environ-
ment with high temperatures and with settle-
ment rates as much  as  3 times that  of  a
corresponding anaerobic  landfill, but a fire
hazard existed.
  5.  The 20-ft-deep landfill, regardless of its
method  of construction,  had  the  greatest
shrinkage  in  the first month following  its
completion. After the  sixth month, the  rates
of settlement  of all the  landfills were  gen-
erally less than 0.05  ft per month.
  6.  Total settlement within the two landfills
arranged for study increased with  total depth;
in this  investigation, doubling the depth re-
sulted in  an  average increase in  total settle-
ment of about 40 percent.
  7.  The  gases  produced within the  an-
aerobic landfills  consisted chiefly of carbon
dioxide and nitrogen.  The concentration of
                                                                                       107

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methane depended upon the moisture  con-
tent and varied from  little more than a trace
in the landfill constructed without the addi-
tion of water to that of a major component
(greater  than 50  percent) in  the saturated
landfill.  Hydrogen was  not present except
occasionally in very small  amounts.
  8. The gases produced within the aerobic
landfill consisted  chiefly of  carbon  dioxide
and  nitrogen. The concentration of oxygen
generally did not exceed 10 percent.
  9. The production of methane was mark-
edly  increased by surface  irrigation  of a
landfill.
  10. The gases  produced within the  four
landfills arranged  for study diffused laterally
and  vertically downward into  the  surround-
ing ground,  as well as upward through  the
top cover.
  11. The initial  peak  temperature within
all landfills was reached within 3 months fol-
lowing the start of construction and occurred
at varying  depths;  no  significantly higher
temperatures were reached thereafter.
  12. The initial temperatures in the aerobic
landfill greatly exceeded those in the anaero-
bic  landfills.
  13. Grasses, shrubs, and trees  were satis-
factorily grown on the surface of  a landfill.
  During the second phase  of this  project,
landfill cells having a  depth of approximately
20 ft were constructed and studied. The fol-
lowing was observed.
  1. Initial landfill  compaction  ratios from
2.1 to 2.2, and an in-place density of 1,000 lb/
cu yd were achieved  .for the three test  cells
A, B, and C. The  in-place density  for cell D
was 634 Ib/cu yd.
  2. Cell A,  receiving  the  Seattle  rainfall
equivalent of 184 in. plus an  extra 30 in. (for
a total of 214 in.  of  water), exhibited some
percolation into the subgrade as evidenced by
a 7  percent  increase  in  the  moisture  of the
subgrade  over that of  undisturbed  soil  at
similar depth. At the  close of the project, the
differential was 12.5 percent.
  3. Cell B, receiving 392 in.  of applied ir-
rigation water, exhibited greater percolation
into the subgrade  as  evidenced by a 15 per-
cent increase in moisture content of the sub-
grade over that of  undisturbed soil at similar
depth. At the close of the 'project, the differ-
ential was 41  percent.
  4. The growth of Bermuda grass was suc-
cessfuly maintained on an anaerobic landfill
with a top earth cover of 2 ft especially pre-
pared to favor turf growth.
  5. The greatest  settlement  (4.25 ft)  oc-
curred in aerobic cell C. The two  anaerobic
cells each settled 2.20 ft.
  6. In anaerobic  cells A and B, after  aging
2 years, the major gas constituents by volume
were carbon  dioxide  and methane  in almost
equal amounts (nearly 50 percent).  Oxygen
and nitrogen  were  present in small, varying
amounts.
  7. Cell C was aerobically operated, and the
gas composition  was  dependent  upon  the
duration of  the blower operation.  The  gas
samples obtained during aeration were char-
acteristically  high  in  nitrogen  and oxygen
and low in carbon dioxide and methane.
  8. The maximum temperature reached in
anaerobic cell A  was  108 F after  79  days.
Over  the final 2 years of  the  more than 4-
year study the temperature  ranged between
53 and 88 F.
  9. The maximum temperature reached in
cell B was 120 F after 31 days. Over the final
2 years of the study the temperature ranged
between 60 and 90 F. Although intended to
be  an  anaerobic  cell,  its performance  was
influenced by the passage of  air from aerobic
cell  C  notwithstanding a 5-ft-wide, contin-
uous adobe-shale  barrier.
   10. The maximum temperature reached in
cell C was 193  F  after 174 days.  Over  the
final  2 years of  the study  the temperature
ranged  between 90 and 164  F.  Bottom tem-
peratures reached peaks high enough to de-
stroy thermistors. Smoke emanations with fire
were noted on a few occasions. The cell tem-
perature was affected by the  aeration cycle.
   11. A cell similar in construction to cell A
or  B  but smaller,  intended  for quantitative
studies  of  gas production, was unsuccessful
although constructed  with extreme  care by
professional plastic fabricators. The polyethy-
lene envelope was not able to store  gas.
   12. The maximum temperature reached in
cell D  was  117  F  after 368 days.  Over  the
final  2 years, the temperature  ranged  be-
tween  67 and 120  F.
108

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  13. Seventy-three cu' yd of refuse packed
into  an  underground  sealed  and  instru-
mented steel  tank produced 2,027  cu ft of
gas,  or  27.7 cu ft/cu yd of refuse,  over  907
days. Virtually all the gas was produced be-
tween the  230th and 600th day.
  14. Final examination of the cell  materials
during  the coring operation  showed the  ref-
use of aerated cell C  to  be well decomposed
except  for plastics and other inerts. In con-
trast, the refuse  of anaerobic cells A and  B
was  easily  identifiable.
  15. Based on the original cell depth of 20
ft, the  volume reduction  achieved  through
aeration amounted to 21.5 percent.  The  vol-
ume reduction achieved in the anaerobic cells
was  11.5 percent.
  16. Epoxy-coated  leads, galvanized  pipe,
and  asphalt-coated steel were found to  be in-
adequate  for  this  type  of investigation. All
seriously  deteriorated  or failed because  of
high  temperatures, corrosion,  or strain ex-
erted by differential settlement.
                PUBLICATIONS

MERZ,  R.  C.,  and  R.  STONE.  Landfill  settlement rates.
Public Works, 93(9): 103, 106, 210, 212, Sept. 1962.

MERZ, R. C., and R. STONE. Gas production in a sanitary
landfill. Public Works, 95(2):84-87, 174-175, Feb. 1964.

MERZ, R. C., and R. STONE. Sanitary landfill behavior in
an aerobic environment. Public Works,  97(1):67, Jan.
1966.

MERZ,  R.  C.,  and  R.  STONE. Progress  report on study
of percolation  through a landfill. Public Works, 98(12):
86, Dec. 1967.

MERZ,  R.  C. and R. STONE.  Quantitative  study of  gas
produced by decomposing lefusc. Public Works, 99(11):
86-87, Nov. 1968.
                  Pollution of  Subsurface Water  by Sanitary Landfills
                         Dr. A. A. Fungaroli
    Advanced  Study  Group for Soil, Water  &
                         Urban Engineering
                           Drexel  University
          Philadelphia, Pennsylvania   19104
 Grant  No. EC 00162-04
 Funds Awarded: $324,268
 Project Period: Sept. 1,  1966 to Aug. 31, 1972
OBJECTIVES:   To provide criteria for the de-
sign of sanitary  landfills in given areas and
under conditions so as  to minimize the pos-
sible  pollution of subsurface water.

APPROACH:   By  use of a controlled labora-
tory  sanitary  landfill,  a  controlled   field
sanitary  landfill, and several active landfills,
located in southeastern  Pennsylvania, models
are being developed to describe the behavior
of sanitary  landfills. The models are  being
used  to  predict landfill behavior  under vari-
ous  environmental  conditions.  The specific
data being  collected are lor landfills located
in  legions   underlain  by  the  Wissahicken
Schist formation.
  The  hydraulics of landfills are being de-
termined with respect to the bulk movement
of water through them and into  underground
soils and water bodies. A computer model  is
being  developed to describe the macroscopic
functioning  of  the landfills and  the under-
ground flow systems. These models will pro-
vide  the  necessary data   to  predict  bulk
movement of leachate through and away from
the landfills. Parameter  influences on  leach-
ate movement are being studied by use of the
models. Among the parameters  being consid-
ered are  landfill  geometry, refuse character-
istics, soil properties, and ground water levels.
   The experimental investigations place ma-
jor emphasis on  the character  of  the  pollu-
tants  carried by  the  leachate  and on the
influence of leachate  quantity on  concentra-
tion of various  ions. Because of the complex
functioning  of  landfills, special emphasis  is
placed  on relationships among the various
ions present.
   The  models  are being  developed so that
they can  be applied to  landfills outside the
                                                                                         109

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investigation area. It is expected that  final
models will be used  in  the determination of
optimum landfill dimensions, soil cover thick-
ness,  potential remedial procedures for exist-
ing leaching landfills, and associated  studies.

FINDINGS:   The  most  advanced  portion  of
this study consists of the data being collected
from the laboratory lysimeter. The moisture-
routing model  for predicting the appearance
of leachate has been  completed and tested by
the  lysimeter.  The  difference  between pre-
diction  time and leachate  appearance is con-
sidered  minimal.  The  model  is  currently
being tested on the field installation.  If  com-
parison  is again  favorable, the model will be
ready for more general application.
   The lysimeter  has provided information in-
dicating that the leachate-carrying pollutants
begin to move out of a landfill as soon  as it
is started.  Although the  initial quantity of
leachate  generation  is  low for landfills  with
low  moisture contents  at  placement,  it can-
not  be  considered  negligible. Further, ion
concentrations  in the  initial  leachate  have
been shown to be substantial.
   The lysimeter results have shown that once
the  refuse system reaches  field capacity, the
total amount of  pollutants removed increases
rapidly. The particular parameters evaluated
are:

LIQUID:  pH,  hardness,   dissolved   oxygen,
phosphate, chloride, sodium, suspended solids,
total residue (total dissolved solids), nitrogen
(ammonia, organic),  nitrate, chemical oxygen
demand, biochemical oxygen demand,  iron,
zinc, copper, nickel, and  sulfate.

GAS:   carbon   dioxide,  oxygen,  nitrogen,
methane,   hydrogen '  sulfide,   and  carbon
monoxide.
  Temperature data  gathered  in the lysim-
eter indicate  that  the system was initially
aerobic  and  reached  temperature levels as
high  as  150  F  shortly  after  activation. A
comparison of lysimeter temperature data and
data gathered  from the  field installation in-
dicates that initial temperature behavior  may
be  a function of unit weight of refuse  place-
ment.   In  the  field,  where the refuse  was
placed at higher unit weight, temperatures
did not  reach the  lysimeter levels and the
refuse  was anaerobic  almost immediately.


                 PUBLICATIONS

REMSON, I., G. H. EMRICH, A.  A.  FUNGAROLI, and A. W.
LAWRENCE. Pollution of subsurface water by sanitary
landfill.  Presented at Engineering  Foundation Research
Conference, Solid Waste  Research and Development, Uni-
versity  School, Milwaukee, July 24-28, 1967. Conference
Preprint No.  B-2.

REMSON,  I.,  A. A.  FUNCAROLI, and  A.  W. LAWRENCE.
Water movement  in an unsaturated landfill. Journal of
the Sanitary  Engineering Division, American  Society of
Civil Engineers, 94(SA2):307-317, Apr.  1968.

SOWERS, G. F. Foundation  problems in sanitary landfills.
Journal of the Sanitary Engineering Division, American
Society  of Civil  Engineers, 94(SA1):103-116, Feb.  1968.
Discussion. Fungaroli, A. A., and R. L. Steiner. Founda-
tion problems in  sanitary  landfills. Journal of the Sani-
tary Engineering  Division, American Society  of  Civil
Engineers, 94(SA4): 764-766,  Aug. 1968.

STEINER, R. L., and  A. A. FUNGAROLJ. Construction of
laboratory and  field facilities  for the investigation of
leaching from sanitary landfills. In Proceedings; Second
Mid-Atlantic  Industrial  Waste Conference,  Philadelphia,
Nov. 18-20, 1968.  Drexel Institute of  Technology, 1969.
p. 301-324.
SUFFET, I., A. A. FUNGAROLI,  R. J. SCHOENBERGER, and
S. LEVY.  Specific  ion electrodes analysis of wastewaters
from solid waste  disposal.  In Proceedings; Third Mid-
Atlantic Industrial Waste Conference, College Park, Md.,
Nov. 12-14, 1969.  University of Maryland, p. 279-303.
 110

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                 Preventing Landfill Leachate Contamination of Waters
                          Mr. Eddie J. Wren
        Department of Environmental  Science
               Gulf South Research Institute
            Baton  Rouge, Louisiana  70808
 Grant No. EC 00393-01
 Funds Awarded: $56,550
 Project Period: Aug. 1, 1969 to July 31, 1971
OBJECTIVES:   To  develop sealant liner ma-
terials that will prevent the escape of leachates
to the surrounding soil  and ground waters
when the leachates are applied to sanitary land-
fills. The  use of low-cost, readily available
waste byproducts as liners is being evaluated.
APPROACH:   A direct-contact survey is being
made of industries concerning  their byprod-
uct waste to determine the location and quan-
tities of these potential barrier materials. Some
of the criteria used for selection of materials
are  particle  and liquid  permeability, inert-
ness,  availability,  cost,  and  handling  and
storage  problems. Laboratory  test cells  have
been constructed for  testing and  evaluating
the effectiveness of the selected barrier prod-
ucts by use of a glass tube and by observation
of cell activities such as moisture gradient and
volumetric changes. Leakage through the cell
liner material into the soil layer beneath will
be monitored by frequent analysis of the soil
beneath the liner  with a water-soluble dye
and a radioactive  tracer placed in the cell
above the sealer.
  Laboratory results will lead to  investiga-
tions  on a small-scale outdoor sanitary  land-
fill where water levels and drainage patterns
are well established. A liner  material  indi-
cated as suitable by laboratory studies will be
used  to  set  up  field cells. A water-soluble
fluorescent  dye,  not  radioisotopes,  will  be
added during the filling operation in order
to check for leaching in  these field studies.
Other parameters for checking leachate loss
as well as contamination of ground water by
the barrier material, will be pH, alkalinity,
suspended  solids, nitrogen compounds, COD,
BOD, DO,  sulfates, sodium, chlorides, TDS,
hardness,  phosphates, nitrate,  calcium,  mag-
nesium, iron, and infrared scanning.

FINDINGS:   The initial screening  of  some 29
industrial products (waste, in most instances)
that  seemed to  be likely  candidates for soil
sealants resulted in 18 of these being retained
and  tested for permeability. All  these prod-
ucts are nonbiodegradable.
  The nonpermeable materials will be tested
in laboratory cells simulating elemental cores
of field landfills.
                   Stabilizing Sanitary Landfills by Injection  Grouting
                        Dr.  Lyle K. Moulton
            Department of Civil  Engineering
                   West Virginia  University
         Morgantown, West Virginia   26506
 Grant  No.  EC 00016-01
 Funds Awarded: $38,929
 Project Period: Feb. 1, 1970 to Jan. 31, 1973
OBJECTIVES:  To determine the effectiveness
of injection grouting of waste material in ac-
celerating the  stabilization of sanitary  land-
fills so that landfill  sites can be reclaimed and
put to use in the shortest  possible time.  It is
anticipated that grouted landfills can be used
not only for parks and playgrounds but also
for industrial,  commercial, and residential
development.

APPROACH:  Various grouting materials with
emphasis on fly ash, bottom ash, and other
                                                                                       111

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wastes with cementaceous characteristics will
be studied to determine their effect on land-
fill  stabilization.  Different grout-refuse com-
binations are  being  studied  to determine
their effect on landfill strength and settlement
characteristics. The influence of various types
of grouts on biological decomposition and
long-term landfill stabilization  is also  being
determined.
  Landfill settlement  characteristics  will  be
studied in the laboratory by use of large con-
solidometers whereby  refuse  cells will  be
loaded  to simulate  various  applied surface
loads. Time  settlement data will be recorded
and leachate analyses  performed. The influ-
ence of grouting on the strength of compacted
refuse will be evaluated by use  of a triaxial
compression apparatus. Samples of refuse will
be compacted into cylindrical molds 6 in. in
diameter  and  12  in. long and  grouted.  At
various intervals the samples  will be tested
for  strength   and  then   microbiologically
analyzed to determine the effect of grouting
on biological decomposition.
  After the laboratory tests,  a limited field
evaluation will be performed. Two small ref-
use cells, about 50 cu ft, will  be constructed.
One is grouted and one  is not. Settlement
records will be kept and  periodic  sampling
and analyses of leachate and gases will be per-
formed to evaluate the effect of grouting.

FINDINGS:  This grant was  awarded Febru-
ary 1, 1970, and findings are not yet available.
                      Thermophilic  Metabolism  in  Solid  Substrates
                  Dr.  Marvin E.  Stephenson
            Department of Civil Engineering
                   Michigan  State University
            East  Lansing, Michigan  90007
 Grant  No.  EC 00292-02
 Funds  Awarded: $72,440
 Project Period: June 1, 1968 to May 31, 1971
OBJECTIVES:  To  investigate  the  principal
variables affecting the decomposition of bio-
degradable   solid  waste  by  thermophilic
aerobic organisms.  Both  macro and  micro
components  of  the  decomposition  products
are measured by using a laboratory model of
the reacting  system.  The study also provides
for the development or  evaluation, or both,
of analytical methodology necessary for  the
physical and chemical   characterization  of
constituents  related  to  the  decomposing
material.
APPROACH:   Laboratory  studies  are  being
carried out in a replicate series of 1.5-cu-ft-
capacity reactors  housed  in  a  controlled-
temperature   module.   Suitable   analytical
methods and  monitoring systems have been
instituted to assay the reactants and products
continuously   during   the   decomposition
process.
  The samples  of  municipal refuse used in
this  project  are collected locally,  sorted to
remove glass and metal materials,  and then
pulverized to particle  sizes  of less  than 1/4
inch. During the decomposition process, the
influent  and exhaust gas  streams  are  moni-
tored chromatographically on a semicontin-
uous basis. Samples of the decomposing mass
are  removed  periodically and analyzed for
organic and  inorganic carbon, organic nitro-
gen, and  moisture content. Analytical  deter-
minations, including pH and nitrate-nitrogen,
are also  performed  on  the liquid fraction of
the sample. The environmental variables that
are controlled or otherwise adjusted are tem-
perature, moisture  content, and air supply.
FINDINGS:  Studies of the assay of solid munic-
ipal refuse indicated that  a  measure of total
organic carbon, rather than  the separation of
the organic carbon complex into constituent
112

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series such as holocellu-lose, crude starch, and
reducing sugars and lipids, provided a  more
satisfactory  estimate of reactive carbon. Ac-
cordingly a wet-combustion method  for  or-
ganic and inorganic carbon was developed to
permit  the analysis of  large   (1-  to   10-g)
samples.
  Preliminary results of the project indicate
that the organic  carbon-nitrogen  ratio  is a
useful parameter  of biologic  stability  and
suggest  its  employment in conventional sani-
tary landfill practices.  Generally,  biological
activities resulting in carbon and nitrogen
losses from  the decomposing mass were com-
pleted within 30 days of the initiation  of the
experiment at all  levels of moisture content
and temperature set. In certain cases signifi-
cant  formation of  nitrate-nitrogen  in the
leachate  (<700  mg/liter)  were   recorded.
  The practical indications of this study sug-
gest the possibility of certain changes in pres-
ent sanitary landfill practices.
  1.  Comminution of the refuse before dep-
osition would increase in-place densities and
provide  a more suitable substrate  for the
promotion of biologic activity necessary for
rapid stabilization of the  fill material.
  2.  Further  consideration  of the develop-
ment of  economical methods of landfill aera-
tion   and  moisture   control  should   be
instituted.
  3.  Practical methods for the establishment
of lower carbon-nitrogen  ratios in raw refuse
would increase the rate of aerobic decompo-
sition of this material.
  4.  Formation of  significant amounts of ni-
trate-nitrogen during the  stabilization process
should be considered, and methods should be
instituted for the  control  of  liquid  passing
through  the fill.
                     Marine Disposal  of Fine-Grained Waste  Solids
                        Dr. M. Grant Gross
            Marine Sciences Research Center
               State  University of New York
              Stony Brook,  New York   11790
 Grant No. EC 00388-01
 Funds Awarded: $89,885
 Project Period: Feb. 1,  1970 to Jan. 31, 1972
OBJECTIVES:  To study the fine-grained waste
solids that constitute about 95 percent of all
waste presently dumped in the coastal waters
of the New York Bight and in  the  estuarine
waters of Long Island Sound. The long- and
short-term physical  and  chemical effects of
these wastes on the ocean water and ocean bot-
tom near the disposal site are being determined.

APPROACH:   A detailed study is being made
on  source,  physical, chemical,  and  mineral
composition  of the  fine-grained wastes prior
to dumping. The  selected  disposal  site  is
being studied for mixing of other types of
sedimentary materials, for physical and  bio-
logical processes  in changing  the character-
istics of the original wastes, and for the effects
of currents and other processes on the final
distribution and amount of material  depos-
ited. Individual waste disposal  operations are
being investigated  by pumping water, down
current from the disposal operation, through
an instrumental chamber where salinity, depth
of sample intake, light transmission, dissolved
oxygen, pH,  and  chlorophyll  are measured.

FINDINGS:   This grant was  awarded on Feb.
1, 1970, and findings are not yet available.
                                                                                       113

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                        Pipe  Transport of Domestic Solid Waste '
                            Dr. Iraj  Zandi
       Towne School of Civil and Mechanical
                               Engineering
                 University of Pennsylvania
          Philadelphia, Pennsylvania   19104
 Grant No. EC-00259-04
 Funds Awarded: $184,234
 Project Period: Sept. 1, 1966 to Aug. 31, 1970
OBJECTIVES:  To  examine  the applicability
of the technology of bulk solid transport in
pipelines to the collection, removal, and treat-
ment of municipal solid wastes.

APPROACH:   Various concentrations and sizes
of ground solid waste were transported, under
pressure, through different size pipes. Opti-
mum particle  size  and  concentration  were
determined with respect to both the engineer-
ing and economic aspects.
   The stochastic  processes governing the gen-
eration of solid wastes were determined, and
their implications on the  design of a pipe sys-
tem evaluated. The cost of  pipeline collec-
tion of solid waste was evaluated with respect
to many factors including population density,
size of collection  area, distance of transport
and type  of disposal.  Domestic  solid waste
services were  economically  evaluated,  and
analytical economic decision models for solid
waste systems were constructed to allow mean-
ingful comparisons  of pipe systems and con-
ventional  systems.
   From the outset it was recognized that for
pipeline  collection  and removal  to be con-
sidered a viable solution  and  an attractive al-
ternative tool for management of  solid waste,
the  following four  distinctly  different  ques-
tions need to be answered.
       1.  Is the collection and  removal of
     solid waste via  pipeline  technologically
     feasible?
       2.  If "solid waste pipeline"  is techno-
     logically feasible, then how does it eco-
     nomically compare  with the  present
     truck collection system?
       3.  If "solid waste pipeline"  is techno-
     logically feasible  and economically  at-
     tractive, then what method of  treatment
     and disposal should be used?
       4.  What   sociopolitical  implications
     may be expected? What governmental in-
    strument  is required to implement  this
    new technology? What would happen to
    present labor force when solid waste col-
    lection  and removal becomes automatic?
Most  efforts were directed toward  answering
the first  two questions in  the  first 31/g years
of the project. Only in the last year  was at-
tention given  to the third question.

FINDINGS:  In regard to the first question, on
the basis of  laboratory experimentation, anal-
ysis of the data,  and field observations, it is
concluded that with present technology both
pneumatic and  slurry  transport of domestic
solid  waste is  feasible. As far as slurry trans-
port is concerned it has been  established  ex-
perimentally that  municipal solid wastes can
be presized  by presently available  shredding
equipment to render them suitable for slurry
transport. It was also established that  slurries
up  to 12 percent solid wastes (paper, cans,
glass,  etc.) can be pumped readily. Pressure
loss data were  collected for  different com-
binations of  pipe  diameter,  mean velocity,
and slurry concentration. A prediction equa-
tion was found that  permitst he prediction of
pressure  losses   with  reasonable   accuracy.
Based on information obtained so far, the de-
tails of which  are reported in the publications
listed, one may conclude that the goals of the
project  in regard  to  laboratory experimenta-
tion on pressurized solid waste pipeline have
been  achieved. The next logical step in  the
study of pipeline under pressure seems to be
a pilot study in the form of a demonstration
project.  Not much useful  information more
than  what is presently available for pressure
solid  waste  pipeline  can be obtained in  the
laboratory.
  In  regard to  economical comparison,  two
separate decisions had to be made:  (1) What
would be the level  of services, that is, fully
automatic  (all  pipeline,  pneumo-slurry   sys-
 114

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tern) or semi-automatic  (truck-pipeline com-
bination)?   (2)   What  type   of  community
would  be selected for comparison? In order
to obtain conclusive  information  it was de-
cided  to select  two  extreme types  of com-
munities, one a  core  of  a large metropolitan
area (center city of Philadelphia) and another
a  residential,  essentially  a  bedroom,  com-
munity  (Radnor,  Pennsylvania,  population
30,000), and  provide  fully automatic services
with access at each  point of  solid waste  gen-
eration. In addition, it was decided to assume
no new technologic  innovations. All  equip-
ment required could be obtained on the mar-
ket.  A detailed, conservative  economic analy-
sis found  the following,  (1) For center city
of Philadelphia the pneumo-slurry (combina-
tion of  pneumatic  and  slurry pipeline) sys-
tem  would  be less expensive than truck collec-
tion over a period of 50 years, if solid waste
has to be transported a distance of more than
50 miles.  (The city  of Philadelphia  is inves-
tigating the   possibility   of   transporting  its
solid waste much further.) (2) For Radnor the
fully automated  pneumo-slurry  system  that
originates from  each house would  cost  con-
siderably more  than  present  truck collection
(slightly  more  than  triple).   If,  however,  a
point of entry should be  provided for a group
of houses, say each four houses, the cost would
compare favorably  with  truck collection.  In
the economic study all components of the cost,
that is,  installation,  operation,  maintenance,
and  amortization are included.  Intentionally
all calculations  are biased in favor of truck
collection in order to establish the real econ-
omy of pipeline  collection and removal.
  In regard to the  third question the  con-
struction of an experimental  facility  is near
completion  for investigating  the  possibility
of using pipeline  as  a biological  reactor  to
treat the solid waste during conveyance.

                PUBLICATIONS

ZANDI, I. Solid waste pipeline. Presented at Engineering
Foundation Research Conference,  Solid Waste  Research
and Development, University School, Milwaukee, July 24-
28, 1967. Conference Preprint No. D-4. 3 p.

ZANDI, I. Collection and removal of municipal solid wastes
by pneumo-slurry system.  Compost  Science,  9(2):7-ll,
Summer 1968.

ZANDI, I.,  and G. GOVATOS. Pipeline  transport  of solid
waste. In  I. Zandi, ed. Advances in solid-liquid flow in
pipes and  its  ^plications. New York,  Pergamon  Press.
(In press.)

ZANDI, I. Pipeline  Collection and removal of solid waste.
Presented  at  Engineering Foundation Research Confer-
ence, Solid Waste Research and Development, II, Beavei
Dam, Wis., July 22-26, 1968. Conference  Preprint No.
A-2.
ZANDI, I., and J. A. HAYDEN. Are pipelines the answer to
waste  collection  dilemma?  Environmental  Science  and
Technology, 3(9):812-819,  Sept. 1969.

YEN,  J. G.,  and I.  ZANDI. Transport  of slurries in
heteiogeneous  regime. Presented at Annual Meeting,  So-
ciety  of Mining Engineers, Washington, Feb. 16-20, 1969.
Conference Preprint No. 69-B-70. 28,  p.

HAYDEN, J. A., P. SEIDENSTAT,  and  1.  ZANDI. Solid waste
generation  and cost in Center City  Philadelphia. Journal
of the Sanitary Engineering Division, American Society of
Civil Engineers. (In press.)

HAYDLN, J. A. Slurry flow—solids transport for the futuie.
Pennsylvania  Triangle,  57(2):22-26,  Nov. 1969.
                                                                                               115

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           SECTION II

    RESEARCH GRANT PROJECTS
STATE AND PRINCIPAL INVESTIGATORS

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                                       RESEARCH GRANT PROJECTS
                                STATE AND  PRINCIPAL INVESTIGATORS *
State

Alabama (1)  .

Alaska (0)
Arizona (0)
California  (15)
Colorado (3)
Connecticut (0)
Delaware (0)
Florida (5)  .  .
Georgia (1)
Hawaii (0)
Idaho (0)
Illinois  (6)
Indiana  (2)

low a  (2)

Kansas (1)  .
Kentucky (0)
Louisiana (3)
Maine (0)
Mar>land (3) .   .
Massachusetts  (4)
Michigan (3)   .  .
tatus
(T)



(T)
(A)
(A)
(T)
(A)
(T)
(T)
(A)
(T)
(T)
(A)
(A)
(A)
(T)
(T)
(A)
(A)
(A)


(T)
(A)
(T)
(T)
(A)
(T)


(A)
(T)
(T)
(T)
(A)
(A)
(T)
(T)
(T)
(A)
(T)
(A)
(T)

(A)

(A)
(T)
(T)
(T)
(A)
(T)
(A)
(A)
(A)
Principal Investigator
Scarsbrook, Clarence E.



Anderson, John R. .
Cogswell, Howard L. .
Barley, Ellis F. . . .
Ecke, Dean H. . . .
Golueke, Clarence G. .
Hart, Samuel A. ...
Hart, Samuel A. ...
Hoffman, Donald A. .
Mercer, Walter A. . .
Merz, Robert C. . .
Oswald, William J.
Rose, Walter A. ...
Snyder, William C. . .
Stephens, Edgar R. . .
Stewart, George F. .
Lindsay, Willard L.
Miller, Byron F. . . .
Updegraff, David M. .


Block, Seymour S. . .
Hortenstine, Charles C.
Knuth, David T. . .
Long, Sterling K. . .
Susag, Russell H. . .
Spradlin, Bobby C. . .


Bryant, Marvin C.
Bugher, Robert D. . .
Charnes, Abraham . .
Day, Donald L. . . .
Pfeffcr, John T. . . .
Sheaffer, John R. . .
Bloodgood, Don E. . .
Dale, Alvin C. . . .
Hazen, Thamoii E. . .
Miner, J. Ronald . .
McKinney, Ross E. . .
Callihan, Cla)ton D. .
Wren, Eddie J. . . .

Wren, Eddie J. . . .

Kramer, Amihud . .
Kruse, Cornelius W. .
Liebman, Jon C. . . .
Fiist, Melvin W. . . .
Saiofim, Adcl F. . . .
Silvciman, Leslie . . .
Wilson, David G. . .
Bocttner, Edward A. .
Gray, Donald H. . . .
Page
4



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State

Minnesota (3) . .


Mississippi (0)
Missouri (1) . . .
Montana (0)
Nebraska (0)
Nevada (0)
New Hampshire (1)
New Jersey (1) . .
New Mexico (0)
New York (8) . .







North Carolina (4) .



North Dakota (0)
Ohio (3) . . . .


Oklahoma (0)
Oregon (3) ...


Pennsylvania (5) . .


Rhode Island (0)
South Carolina (2) .
South Dakota (1) .
Tennessee (0)
Texas (2) ....
Utah (0)

Vermont (0^

Virginia (2) ...

Washington (1) . .
West Virginia (5)




Wisconsin (1) ...
W)oming (0)
Status
(A)
(T)
(A)
(A)

(A)



(A)
(T)

(A)
(A)
(A)
(A)
\ /
(A)
(T)
(T)
(T)
(T)
(A)
(A)
(A)

(A)
(T)
(T)

(A)
(A)
(A)
(A)
(A)
(T)
(A)
(A)

(A)
(A)
(T)
(A)
(A)



(A)
(A)
(A)
(A)
(A)
(T)
(T)
(A)
(T)

Principal Investigator
Stephenson, Marvin E. .
Bond, Richard G. . .
Bond, Richard G. . .
Diesch, Stanley L. . .

Malisch, Ward R. . .



Grethlein, Hans E. . .
Besley, Harry E. . . .

Gross, M. Grant . . .
Grove, Cornelius S.
Heimburg, Richard W.
Jeris, John S 	
Kaiser, Elmer R. . . .
Kaiser, Elmer R. . . .
Kaiser, Elmer R. . . .
Sinister, William W. .
Axtell, Richard C. . .
Caller, William S. . .
Hill, Charles H. . . .
Leatherwood, James M.

Miller, Paul D. . . .
Taiganides, E. Paul .
Taiganides, E. Paul .

Currier, Raymond A. .
Freed, Virgil H. . . .
Klein, Donald A. .
Fungaroli, A. Alexander
Morgan, Peter E. D. .
Purdom, P. Walton .
Thygeson, John R. .
Zandi, Iraj 	

Andrews, John F. . .
Hulbert, Samuel F. . .
Berry, Edward C. . .
Howes, James R. . .
Myrick, H. Nugent . .



Fontenot, Joseph P.
Kelly, James L. . . .
Allan, G. Giaham
Bailie, Richard C. . .
Buichinal, Jerry C. . .
Burchinal, Jerry C. . .
Burchinal, Jerry C. . .
Moulton, Lyle K. .
Witzcl, Stanley A. . .

Page
112
36
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35

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82
27

113
92
49
8
42
46
68
72
51
6
87
100

48
16
21

96
76
83
109
77
41
34
114

93
17
27
31
16



99
87
102
81
40
105
106
111
18

  * See page 131 for complete listing of research and  training grant principal investigators.
   ("I")  Terminated
   (A)  Acti\e
as of March 31, 1970.
                                                                                                         119

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   SECTION III



TRAINING GRANTS

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                     Dr. William W.  Shuster
            Department of Civil  Engineering
            Rennselaer Polytechnic  Institute
                    Troy, New York   12181
  Grant  No.  EC 00005-03
  Funds  Awarded: $131,088
  Project Period: July 1,  1967 to June 30, 1972
PROGRAM:   This  training  program  estab-
lishes an area of specialization,  primarily at
the M.S. level, in solid waste disposal within
the existing programs in environmental engi-
neering.  It  is aimed at providing personnel
trained to  assume responsibilities  in the  su-
pervision,  planning, and  administration  of
solid waste management facilities. The study
plan for  each student is arranged by the stu-
dent advisor in consultation with the student.
Course requirements are flexible,  and every
effort is made to satisfy the interests and ob-
jectives of  the candidate consistent  with  his
background and degree of  preparation.
  Courses  initiated  under this grant and  re-
quired of the students participating in this pro-
gram include one entitled Solid Wastes and
one  entitled Solid  Wastes Laboratory. The
Solid Wastes course deals with  the  prepara-
tion of refuse  for collection, costs of collec-
tion, collection methods and equipment, spe-
cial refuse problems, disposal and treatment
methods,  and diseases associated with garbage
and refuse.  The  Solid  Wastes  Laboratory
course covers experiments in solid wastes dis-
posal, techniques for sampling and methods of
analysis of solid wastes, chemical and physical
changes in composting, leach  studies,  meth-
ods of odor control, and landfill and incinera-
tion procedures.  Other  courses, including
Unit  Processes, Atmospheric  Pollution,  and
Planning  for Waste  Disposal and Pollution
Abatement,  cover  subjects related to  solid
waste management.
  A thesis or project is required of candidates
for a degree  in  solid wastes.  The thesis or
project is  expected  to be related to solid waste
management.
  To date, 11 students have completed solid
waste courses and 6 have been supported by
traineeships.
                      Dr.  P. Walton Purdom
         Center for Study of the Environment
                          Drexel University
          Philadelphia, Pennsylvania   19104
 Grant No. EC  00006-04
 Funds Awarded: $176,789
 Project Period: July 1,  1966 to June 30, 1971
PROGRAM:   This  program  provides  profes-
sional  education at the masters level for stu-
dents concerned with the solution of prob-
lems   associated  with  solid  wastes.  The
instructional    plan    produces   graduates
equipped to  manage the local government
units that collect and dispose of solid wastes,
to organize  and administer State and Federal
programs for  the  promotion of  acceptable
solid  waste  collection and disposal practices,
and to staff  other  agencies and  consulting
engineering offices.
   The  educational  program is designed to
cover in depth the  characteristics of wastes,
systems for collection and disposal, theories
that form  the basis of design  of  disposal fa-
cilities,  pertinent  management  techniques,
and the relationships of solid wastes to other
environmental  problems.  Faculty  members
from the various engineering and science de-
partments participate in this program. On the
successful completion of course requirements,
participating students receive  a master's de-
gree  in environmental  engineering, science,
or civil engineering, depending upon the elec-
tives selected and prior education.
   Specific  courses  directly  related  to  solid
waste  management  being  offered  are: Solid
                                                                                       123

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Waste Analysis, Solid Waste Systems,  Com-
bustion Theory, Incinerator Design, and En-
vironmental Systems  Analysis.  Other courses
offered that have  some relationship to  solid
waste management practices include  air pol-
lution, water pollution, and microbiology.
  To date,  18 students have been supported
by solid waste traineeships. Five of the train-
eeship-supported students are currently en-
rolled in graduate programs at Drexel.
                       Dr. Russell H.  Susog
    Department of Environmental Engineering
                       University  of Florida
                 Gainesville, Florida   32601
 Grant No. EC 00007-03
 Funds Awarded: $131,094
 Project Period: July 1, 1967 to June 30, 1972
PROGRAM:   This program is designed to pro-
vide training of field personnel for design and
operation of solid waste programs  as well as
training of research personnel for  the devel-
opment of basic data needed to design  well-
functioning solid waste management systems.
The board of regents has given the university
the responsibility  to provide  technical assist-
ance to  city, county, and regional  planning
agencies;  health  departments; governmental
units;  private  companies;  and  individuals.
Through the training  program, a reservoir
of  trained  personnel  will  be  developed to
meet these needs.
  It is anticipated that the solid waste trainees
will be from the engineering and life sciences
disciplines.  They will  be  supported at the
M.S. level and major in environmental  engi-
neering  with a specialization  in solid waste
management with  thesis or special problem
work in solid waste research.
  Special problem courses and  two specific
solid  waste  courses  are  offered.  One course
entitled  Solid  Wastes covers  the following
subject  areas:  quantities and  characteristics
of  municipal  refuse;   collection  methods,
equipment,  and  costs;  refuse  disposal  prac-
tices;  and regional  planning and  manage-
ment. To date this course has been offered
six  times with  a total enrollment of 52 stu-
dents.  The  other course, Analysis  of  Solid
Wastes has been  recently offered with an en-
rollment of  three students. Subject areas cov-
ered  in  this  course include: physical  and
chemical  analysis of refuse,  calorific  value,
organic  content,  biodegradability,  oxygen
and nitrogen  requirements,  and  identifica-
tion of  flora and fauna  associated with com-
posting.  A  third course  offering,  Design of
Solid  Waste Management Systems,  is  being
developed.  Three  students  have  been sup-
ported by solid waste traineeships to date.
                    Prof. Eugene A. Glysson
               Civil Engineering  Department
                     University of Michigan
               Ann Arbor, Michigan   48104
 Grant No. EC 00008-04
 Funds Awarded: $144,857
 Project Period: July 1,  1966 to June 30, 1971
PROGRAM:   This  solid  waste  training pro-
gram is designed to attract and train profes-
sional  personnel who will be  better able to
apply  up-to-date knowledge  needed  to man-
age solid waste material properly. The pro-
gram,  administered through the  civil engi-
neering  department,  includes  participation
from  other disciplines such as the environ-
mental  health  department of the school of
public health  to  provide for an  interdisci-
plinary approach to the solution of solid waste
management problems. Students enrolled in
124

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the courses  come from  the .college of engi-
neering and the school  of public health as
well as the school of natural resources.
  Two solid waste courses are offered. One,
entitled Solid Wastes Engineering, deals with
the engineering  and design of methods  for
collection and disposal of  the solid wastes of
urban communities and  the related effects of
such collection and  disposal  on the environ-
ment. The other course, Special Problems in
Solid Wastes Engineering,  covers the  applica-
tion  of  principles  presented  in the  Solid
Waste Engineering course  to engineering  and
environmental  health problems in  the  col-
lection and  disposal  of solid  wastes.  Compre-
hensive analyses and reports are assigned  on
an  individual student basis. Typical special
problems include  studies related to refuse
collection,  refuse  characteristics,  incinerator
emissions,   landfill   stability,    incinerator
quench  water  characteristics,  and  regional
solid waste management.
  To  date  the   Solid  Waste  Engineering
course has been elected by 54 students over
a 6-year period.  The  Special  Problems  in
Solid Waste Engineering course has  been
elected  by 26 students over  the last  4 years.
There has been a total of 16 graduates  from
this program, 9 being supported by this train-
ing grant.
                   Professor  Raul  Zaltzman
            Department of Civil Engineering
                    West Virginia University
                 Morgantown, West Virginia
 Grant No. EC 00009-03
 Funds Awarded: $181,854
 Project Period: Jan. 1, 1967 to June 30, 1972
PROGRAM:   One  purpose of this  program is
to provide the student with an understanding
of the needed design engineering aspects both
of existing  methods  of  solid waste manage-
ment and of methods that are relatively new
in application. Another purpose  is to  intro-
duce  improved  design criteria  and disposal
methods that will optimize  current  opera-
tions  and provide for adequate  disposal of
solid wastes resulting from other waste treat-
ment systems.
  Three courses  are  offered by the civil en-
gineering program dealing with  solid  waste
management problems; two of them deal ex-
clusively with solid wastes and the  third offers
the students an  opportunity to  integrate the
information  gained throughout their  study
program in  one major interdisciplinary  exer-
cise  of  total environmental planning.  This
last course  is conducted by the  solid  waste
management and the  urban  transportation
staff with assistance of most of the civil  engi-
neering staff on consulting and guest lecture
basis. Two other courses, Design of Dynamic
Material Systems and Design of Solids  Han-
dling Systems, offered by the Departments of
Industrial Engineering  and  Chemical  Engi-
neering,  respectively, include various aspects
of solid waste management as the major por-
tion of the  subject matter. The  Elements of
Solid Waste Management course offered  by
the Civil Engineering Department covers basic
solid waste  material, including the study of
traditional  patterns  and problems of solid
waste storage, transport, and disposal; a  dis-
cussion  of  field evaluation  techniques  for
existing  systems  and facilities; an  examina-
tion of engineering alternatives  with appro-
priate  consideration for  air pollution  control
and land reclamation;  analytical approaches
to recovery,  conversion, and reuse  of mate-
rials; and the application of systems analysis
concepts to solid wastes handling  and disposal
systems.  Sixty-two  students  have completed
this course  through  the fall  of 1969.  The
other course offered by the Civil  Engineering
Department  related  to  solid waste manage-
ment is  Municipal and  Industrial  Design of
Solid Wastes Disposal Operations. This course
includes  a comprehensive study and  review
of  design criteria  for the existing methods
and equipment used  for the  disposal of solid
wastes  generated by industry and municipali-
                                                                                      125

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ties.  The operations studied are subdivided
into  those accomplishing on-site preparation,
volume and density modification, and salvage
or reclamation (or both) of ferrous and non-
ferrous metals and other  marketable mate-
rials. Also included are  studies of the storage
and  handling  practices and  equipment  in-
volved  in  these  operations.  This  course is
being  offered during the spring of  1970  for
the third time with a total enrollment of 29
students for this lapse. In addition  to  the
courses offered, 48  guest speakers have  pre-
sented their views of solid waste management
practices to  interested, students and  faculty.
The guest speakers have come from  private
industry,  governmental  agencies,  and  other
universities.
  With the  assistance of  this grant,  12 stu-
dents have been  directly supported,  and  4
others have received partial support through
assistantships. There are 11 students currently
enrolled in  a  graduate  study program with
emphasis   on  solid  waste management;  of
these, 5 are being supported with traineeships
provided by  this grant and 1  is receiving par-
tial support.
                    Dr. Joseph F. Molina, Jr.
              Department of Civil Engineering
                     The University of Texas
                       Austin, Texas  78712
  Grant No. EC 00010-04
  Funds Awarded:  $235,313
  Project Period: July 1, 1966 to June 30, 1971
PROGRAM:   This training grant has provided
a basis for the development of an  environ-
mental health engineering program with spe-
cial  emphasis on solid waste management. A
multidisciplinary  program with specific em-
phasis on  the  application of new engineer-
ing  principles  and  processes to the solution
of solid waste problems,  as well as an aware-
ness of the  significance  of  proper planning
management and sociological considerations,
particularly  in  the case  of  municipal solid
waste  systems, has evolved. This program in-
cludes  the training of graduate students by
course work and research to solve real prob-
lems, the development of a competent health-
related teaching and research training pro-
gram, and the  opportunity for both  faculty
and students to study new approaches to the
disposal of solid  wastes  resulting from mu-
nicipal and industrial activities. Participation
of students and faculty of the Chemical  En-
gineering Department is  providing the means
for  the exchange  of  information related to
the  development  of new processes or to the
application of  existing  processes  to  systems
of recycling components  of the refuse or to
disposal systems.
   The objectives of this program are being
satisfied by formal  courses, special seminars,
and particular research  projects  that  deal
with a broad spectrum of solid waste manage-
ment,   collection,   and  disposal  problems.
Trainees sponsored under the auspices of this
project at present are all master  of science
candidates  who are  pursuing  program-pre-
scribed course work in environmental health
or  in civil or chemical engineering. A thesis
related to solids problems is required of each
trainee.
   The  course  initiated under this grant, en-
titled  solid  waste  disposal,  deals with  the
production, collection, and disposal of munic-
ipal waste.  To date,  33 students have  com-
pleted this  course  and 11 trainees  have  been
supported by this grant.
                PUBLICATIONS
 Environmental Health Engineeiing Research Laboratory.
 Unpublished data. [EHE 01-6801, CRWR-24], [Jan. 1968],
 Austin, Texas.

 Environmental Health Engineeiing Research Laboratoiy.
 Unpublished data.  [EHE 08-6801],  [Aug. 1968], Austin,
 Texas.

 Environmental Health Engineering Research Laboratory.
 Unpublished data. [EHE 10-6801, CRWR-30], [Oct. 1968],
 Austin, Texas.
 126

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Environmental Health-Engineering Research Laboratory.
Unpublished data. [EHE 11-6801, CRWR-32], [Nov. 1968],
Austin, Texas.

Environmental Health Engineering Research Laboratory.
Unpublished data. [EHE 69-02, CRWR-35], [Nov. 1968],
Austin, Texas.
Environmental Health Engineering Research Laboratory.
Unpublished data. [EHE  68-13], [Apr.  1969], Austin,
Texas.
Environmental Health Engineering Research Laboratory.
Unpublished data. [EHE  70-01], [Jan.  1970], Austin,
Texas.
                          Dr.  Ross McKinney
              Department of Civil Engineering
                        University of Kansas
                   Lawrence, Kansas   66045
 Grant No. EC 00011-03
 Funds Awarded: $116,705
 Project Period:  July 1, 1967 to June 30, 1972
PROGRAM:   This  training program provides
graduate engineers  at  the M.S. level  with a
background  in solid  waste management  for
employment  in  State  health  departments,
county  sanitation  districts,  municipalities,
consulting  engineering  firms,  and  Federal
agencies.  Graduate engineers  at the  Ph.D.
level are trained to conduct research in solid
waste management and to teach. Graduate
trainees come from the various engineering
departments  and  from  the science  depart-
ments. Each trainee is expected to complete
a research  thesis related to some aspect of
solid waste management.
  Presently  one   solid  waste  management
course,  entitled Solid  Waste Disposal, is  of-
fered.  This course  covers most aspects  of
solid  waste  management, including  charac-
teristics of solid  wastes,  storage, collection,
sanitary landfilling, incineration, composting,
salvage  and reclamation, and  organizational
structure of various local,  State, and Federal
agencies involved in solid waste management.
Special  problems  courses  are also  offered
wherein students  are encouraged  to make
special investigations  into a particular solid
waste-related problem. The special problems
permit  the  student to expand his knowledge
in specific areas of interest.
  During the past 3 academic years the solid
waste disposal course has been offered once
each year. Thirteen students have completed
this  course  and 9 are  about to complete it.
During these 3 years, six students have taken
the  special problems course and conducted
individual research in  countywide collection
and  disposal, routing  of  collection vehicles,
and  chemical analysis of refuse. To date three
trainees have been supported by this  grant,
one  at the master's level and two at  the Ph.D
level.
  This program has assisted in> the  establish-
ment of a cooperative  arrangement with the
city  of Lawrence.  Currently, a Ph. D. student
is  supported  one-half time  by  the  city as a
special  assistant  for solid wastes  in the de-
partment of public works.
                PUBLICATIONS

TILSWORTH, T. Garbage, ten million pounds a day  and
growing. In Proceedings;  Governor's Conference on  En-
vironmental Problems, Topeka, Dec. 11, 1969. Kansas
State Department of Health, 1970.  p. 39-47.
                      Dr. H. Nugent Myrick
               Cullen  College of Engineering
                       University of Houston
                     Houston, Texas  77004
 Grant  No.  EC 00012-02
 Funds  Awarded: $103,959
 Project Period: July 1, 1968 to June 30, 1971
PROGRAM:   This  grant ensures the develop-
ment of a  high-quality  educational and re-
search program in  the monitoring,  collection,
and  conversion of solid wastes in  the' urban
                                                                                         127

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environment.  The breadth  of  the  program
includes training and  research for biologists,
chemists, and all types of engineers;  however,
particular  concern is  given  to ensure  the
continued  in-depth study  in  the  trainees'
initial or desired basic scientific or  engineer-
ing study discipline. Research undertaken by
the  trainees is related to  the solution  of
problems  of   highly   industrialized  urban
environments.
  Trainees supported by  this  grant are re-
quired  to  complete a  thesis  related to some
aspect of solid waste management and to com-
plete the solid waste  courses offered by  the
University  of Houston. The titles of the solid
waste courses  to be offered  and a  summary
of course content follows:  Solid Wastes and
Measurements, lecture and laboratory experi-
ments related to the monitoring and  measure-
ment of solid  wastes  and their residues  in
the  environment and  on  the  conversion of
solid wastes by conventional and  advanced
technology; Solid Wastes Conversion Processes,
lectures on the theory of • conversion  process
units,  process  design,  economic  analysis of
processes,  and  model  assimilation of  solid
waste conversion systems; Solid Waste Collec-
tion System Analysis, lectures on conventional
practice  and  advanced technology of  solid
waste collection, including model assimilation
of  the generation and collection of  solid
wastes; Environmental Sciences and Engineer-
ing  Seminar, seminars on the various perti-
nent topics or  the technology, management,
and science of air, water, and terrestrial pollu-
tion of urban environments.
  Through the academic year of 1968-1969,
only the Solid Waste Conversion  and Process-
ing course was offered. The total enrollment
in this course  was nine students, including
seven  part-time students  from industry  and
consulting offices.  To date, two students  have
been  supported by  traineeships  from   this
grant.  Both are expected to graduate with an
M.S. degree in  1970.
                 Dr. Richard  S. Engelbrecht
            Department of Civil Engineering
                       University of Illinois
                    Urbana, Illinois  61801
 Grant No. EC 00032-02
 Funds Awarded: $85,458
 Project Period: July 1, 1968 to June 30, 1973
PROGRAM:  This training  program  provides
graduate students the opportunity of becom-
ing knowledgeable about solid waste problems
and  solutions so that they may be prepared
to make a contribution  to the field of solid
waste management.  This  training  program
embraces  an  interdepartmental approach in-
volving sanitary engineering, food science,
and agricultural engineering. The program is
limited to the  M.S.  level,  and  trainees re-
ceive a degree in one of  the participating de-
partments. All  candidates for work in this
area are expected  to fulfill requirements in
their own discipline, but  as an integrating
force, these same aspirants will be expected
to  complete   the  following   three  common
courses:  (1)  Sources and  Characteristics of
Solid Waste,  (2)  Solid  Waste Management
and  (3) Environmental  Health Engineering,
and to show necessary orientation in the area
by virtue of submitting an  approved  thesis
or independent study related to a solid waste
problem. A special and separate seminar will
be developed that will  serve also to knit the
program  together. Outside  speakers  whose
work relates directly to this area will further
stimulate interest  and challenge the progress
of the student.
  An  interdepartmental  approach  to this
problem was  used because of  the  close re-
lationship  of  the  respective departments  to
the solid waste problem.  The  participation
of the Department of Agricultural  Engineer-
ing in  this approach  is desirable  owing  to
the tremendous solid waste problems created
by the agricultural community and  their de-
sire to solve these problems.
 128

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  The food processing industry, from canning
to the  frozen food operations, produces many
wastes  of various types that need to be prop-
erly managed. Therefore the participation of
the department  of food science  is  important
in the  success of this training program. The
participation of  the Department of Civil En-
gineering in  this program is needed to pro-
vide an integrated  approach in   enhancing
municipal, agricultural,  commercial, and in-
dustrial waste management.
  The two  solid waste courses  have had an
average enrollment of eight students each. So
far, four students have been supported by this
grant, two working toward their M.S. in sani-
tary engineering, one toward an M.S. in agri-
cultural engineering, and one toward an M.S.
in food science.
                   Dr. Frederick G. Portland
                School of  Civil Engineering
            Georgia Institute  of  Technology
                  Atlanta,  Georgia  30332
PROGRAM:  This program provides specialized
interdisciplinary training in solid waste tech-
nology founded upon the basic  and applied
sciences associated with present and  proposed
methods of solid waste collection, transporta-
tion,  and treatment. The training includes
emphasis  on  pertinent unit  processes  and
operations, system analysis and optimization,
economic analysis and financing, and program
administration. This emphasis  is accentuated
by a core curriculum  in solid waste technol-
ogy,  by suggested  graduate curricula in each
contributing discipline, and  by the  use  of
seminars and  special  workshops. Solid waste
trainees come  from various schools, including
those of civil engineering, industrial engineer-
ing, social sciences, and city planning, and will
receive degrees from their respective schools.
  Three solid waste courses are offered  at
Georgia Institute of Technology, Solid Waste
Technology I  and II plus a Special Problems
course.  Solid  Waste Technology I  is an in-
troduction to the fundamentals of solid waste
characterization,  handling and disposal sys-
 Grant No. EC 00033-04
 Funds Awarded: $139,679
 Project Period: July 1,  1966 to June 30,  1974
terns, physical and chemical methods of solid
waste analysis, treatment  methods, manage-
ment and  design principles,  environmental
impact, and control procedures.  This course
has been offered  three times with a total en-
rollment of 21 students.  Solid Waste Tech-
nology II is related to the evolution of typical
solid waste problems,  the application of de-
sign and management  principles, case studies
of operational solid waste  systems, and  the
study of new methods and advanced  topics.
This course has also been offered three times
and has had a total enrollment of 19 students.
In addition to formal classes, students are ex-
posed  to solid waste  management practices
by special seminars with guest speakers. About
20  different  guest speakers have  addressed
seminars to date.
  During the four years of this grant, eleven
students have  been supported by  traineeships.
Of  the six  students that have graduated,  five
are now employed by  governmental agencies
and one by private industry.
                  Dr. Nathan  C. Burbank Jr.
      Department  of  Environmental  Health
                       University of Hawaii
                  Honolulu,  Hawaii  96822
PROGRAM:   This grant  provides  the means
for  the  introduction  of  three  major  new
 Grant No. 00038-01
 Funds Awarded: $49,223
 Project Period: July 1, 1969 to June 30,  1972
courses related to solid waste management for
students of environmental sanitation into the
                                                                                      129

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curriculum of the  Department of  Environ-
mental Health of the School of Public Health.
The course provides comprehensive instruc-
tion in the technical, economic, and geogra-
phic factors of importance to the design and
management of solid waste systems.  Student
trainees have  the option  of working toward
a master of public health or a master of sci-
ence  degree.  Trainees who  wish to  obtain
an M.S. degree must do  a thesis related to a
solid  waste  management problem.  Those
working toward  an  M.P.H.  degree  are  not
required to submit a thesis  but will be re-
quired  to  obtain  field experience  in solid
wastes, e.g., work with  personnel of  the State
health department.  Further,  they will be re-
quired to organize, prepare, and submit docu-
ments describing  and  commenting  on their
field experience.
  The new courses  in  solid waste  manage-
ment and a brief description of each follows:
Solid Waste Management and Control, covers
the necessity  of  proper solid waste manage-
ment from a public health standpoint as well
as an introduction of waste generation, stor-
age, collection,  utilization, and disposal of
solid  waste.  The Sampling and Analysis of
Solid Wastes  course introduces  the student
to  physical and  chemical methods of solid
waste analysis. The  course Design of Solid
Waste  Disposal  Facilities  incorporates  the
solution of problems associated with incinera-
tion, sanitary landfilling, composting, reclama-
tion,  and  the  various  aspects  of  refuse
collection and transportation.


               PUBLICATIONS

BURBANK,  N. C., JR. The importance  of sanitation  as
applied to the  tourist  industry in  Hawaii.  Professional
Sanitation Management, l(4):55-59, Jan.  1970.
MCCAULEY, R. F., N.  C. BURBANK, JR., and R. H.  F.
YOUNG. Production of charcoal from bagasse. Presented at
National  Industrial Solid Waste  Management Conference,
University of Houston,  Mar. 24-26, 1970.
 130

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         SECTION IV

RESEARCH AND TRAINING GRANT
   PRINCIPAL  INVESTIGATORS

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                            RESEARCH AND TRAINING GRANT
                               PRINCIPAL INVESTIGATORS
Principal Investigator
Page    Principal Investigator
Allan, G. Graham	102
Anderson, John R	52
Andrews, John  F	   93
Axtell, Richard C	51
Bailie, Richard C	   81
Berry, Edward C	   27
Besley, Harry E	27
Block, Seymour S	   71
Bloodgood, Don E	58
Boettner, Edward A	   45
Bond, Richard  G	36, 39
Bryant,  Marvin  C	74
Bugher, Robert D	13
Burbank, Nathan C	129
Burchinal, Jerry C	40,  105, 106
Callihan, Clayton D	   90
Charnes, Abraham	56
Cogswell, Howard L	102
Currier,  Raymond  A	96
Dale, Alvin C	   19
Darley, Ellis  F	   84
Day, Donald  L	   25
Diesch, Stanley L	   35
Ecke, Dean H	   50
Engelbrecht,  Richard S	128
First, Melvin W	43
Fontenot, Joseph P	99
Freed, Virgil H	76
Fungaroli, A. Alexander	109
Caller, William S	    6
Glysson, Eugene A	124
Golueke, Clarence G	60
Gray, Donald H	82
Grethlein, Hans E	82
Gross, M. Grant	113
Grove, Cornelius S	92
Hart, Samuel A	15, 29
Hazen, Thamon E	23
Heimburg, Richard W	   49
       Hill, Charles  H	87
       Hoffman, Donald A	   69
       Hortenstine, Charles C	    8
       Howes, James R	   31
       Hulbert, Samuel F	   17
       Jeris, John S	    8
       Kaiser, Elmer R	42,  46, 68
       Kelly, James L	   87
       Klein, Donald A	   83
       Knuth, David T	    5
       Kramer, Amihud	95
       Kruse, Cornelius W	   57
       Leatherwood, James M	100
       Liebman, Jon C	   55
       Lindsay, Willard L	   12
       Long, Sterling K	   70
       McKinney,  Ross  E	15, 127
       Malina,  Joseph  F., Jr	126
       Malisch, Ward R	   94
       Mercer, Walter A	    3
       Merz, Robert C	107
       Miller, Byron F	73
       Miller, Paul D	48
       Miner, J.  Ronald	30
       Morgan, Peter E. D	   77
       Moulton, Lyle K	Ill
       Myrick,  H. Nugent	16, 127
       Oswald, William  J	85
       Pfeffer, John T. '	88
       Pohland, Frederick G	129
       Purdom,  P. Walton	41, 123
       Rose, Walter A	11
       Sarofim, Adel F	47
       Scarsbrook, Clarence  E	    4
       Sheaffer, John R	   63
       Shuster, William W	72, 123
       Silverman, Leslie	38
       Snyder, William C	66
       Spradlin, Bobby C	54
                                                                                   133

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Stephens,  Edgar R	24   Updegraff, David M. . •	78
Stephenson, Marvin  E	112   Wilson, David G	   89
Stewart, George F	    14   Witzel, Stanley A	   18
Susag,  Russell H	65, 124   Wren, Eddie J	72,  111
Taiganides, E. Paul	16, 21   Zaltzman, Raul	125
Thygeson, John R	    34   Zandi, Iraj	114
                                                U.S GOVERNMENT PRINTING OFFICE 1971 O - 4I3-24O
 134

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Envirsnm,~.*r;"r:.l ?rrt3ction Agency
Lil.r:,.-.;,   .   . •   '
1 Iforoh  w;.c  .v  jl-rive
Chicago,  Illinois   60606

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U.S. ENVIRONMENTAL PROTECTION AGENCY

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