SW661
Solid Waste Management Abstracts From The Literature, 1965
228
1972
NEPIS
online
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20060822
hardcopy
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refuse waste disposal sludge wastes public collection plant city water solid percent composting incineration cleansing system removal new paper one
Connoll, John A. ; Stainbac, Sandra E. ; Environmental Protection Agency, Rockville, Md. Solid Waste Management Office.
Solid waste disposal; Bibliographies; Abstracts;
The literature represented in this bibliography does not include all the 1965 solid waste literature published; 58 periodical and 51 nonperiodical titles covering both the foreign and domestic literature were screened for inclusion. No effort was made to separate strictly technical material from that which is more general. The bibliography is arranged in categories corresponding to the various administrative, engineering, and operational phases of solid waste management. Indices include subject, corporate author, and geographical location cited. Addresses of periodical cources are provided. (Modified author abstract)
SOLID WASTE
MANAGEMENT
Jibs tracts from the dotteraturt
1965
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SOLID WASTE MANAGEMENT
c/tbstracts from the Jotterature — 1965
This publication (SW-66.1) was prepared by
JOHN A. CONNOLLY and SANDRA E. STAINBACK
U.S. ENVIRONMENTAL PROTECTION AGENCY
1972
Environmental Protection Agency
Library, Legion V
1 Hearth VTacker Drive
Chicago, Illinois 60606
For sale by the Superintendent of Documents, U.S. Government Printing Ollice, Washington, D.C., 20402 - Price *!.'
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Note: The Federal solid waste management program is unable to
furnish reprints of the cited publications, with the exception of
papers authored by program personnel. If copies of publications
are not available in local libraries, readers should contact the
author(s) or publisher to obtain reprints.
An Environmental Protection Publication
This publication is also in the Public Health Service numbered
series as Public Health Service Publication No. 91-1965, Supple-
ment H; 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. 53-60514
ENVIRONMENTAL PROTECTION AGENCY
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THE SOLID WASTE MANAGEMENT BIBLIOGRAPHIC SERIES
1941 - 1971
Since its beginning over a quarter century ago, the
Federal program in solid waste management has had a number
of organizational aegises, as well as several organizational
titles. One constant, though, has been quite visible through-
out the program's development, and that is its unflagging
~~". interest in bibliography.
> % ,
Collecting past data on a problem by a literature search
. is the classic first step used in the scientific method of
1/7
,P, problem solving. Thus, in 1941, the first workers in the
$ Federal program searched the world-wide literature for infor-
^W mation that had been published on solid wastes. The resultant
bibliography was then published as a service to other workers
l^ in the field and became an annual publication in the Public
Health Service series. This step was taken again in 1965,
r~- following the passage of the Solid Waste Disposal Act, when
,-y, the early bibliographies were reprinted and made more widely
available. The literature search was then extended through
1971, and the present bibliography is one of those that will
*
bring the series up to date.
-SAMUEL HALE, JR.
Deputy Assistant Administrator
for Solid Waste Management
111
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SOLID WASTE MANAGEMENT
Abstracts from the Literature
1965
The Solid Waste Disposal Act of 1965 (Public Law 89-272,
Title II) and its amending legislation, the Resource Recovery
Act of 1970 (Public Law 91-512, Title I), authorize collection,
storage, and retrieval of information relevant to all aspects
of solid waste management.
The literature represented in this bibliography does not
include all the 1965 solid waste literature published; 58 peri-
odical and 51 nonperiodical titles covering both the foreign
and domestic literature were screened for inclusion. No effort
was made to separate strictly technical material from that
which is more general. The bibliography is arranged in cate-
gories corresponding to the various administrative, engineering,
and operational phases of solid waste management. Indices
include subject, corporate author, and geographical location
cited. Addresses of periodical sources are provided.
This project is the result of the combined efforts of the
Solid Waste Information Retrieval System (SWIRS) and the Franklin
Institute Research Laboratories under contracts PH 86-67-182
and PH 86-68-194. SWIRS was also assisted in this project by
1970 summer-student employees: Cynthia Brooks, Susan Brown,
and Martha Renner.
—THOMAS F. WILLIAMS, Director*
Technical Information Staff
Office of Solid Waste Management
v
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CONTENTS
Page
Regulations (including Laws and Ordinances) 1
Finances (including Costs, Fees, Taxes, etc.) 6
Storage (including Methods and Equipment) 8
Collection and Disposal—General 13
Collection and Transportation of Refuse 24
Disposal—General 32
Agricultural Wastes 46
Automobile Disposal 48
Composting 53
Reduction 70
Incineration 74
Incineration—Europe 84
Industrial Wastes 93
Hazardous Wastes (including Pesticides) 138
Salvaging 140
Sanitary Landfill 151
Street Cleaning 159
Education and Research 163
Health and Safety 165
Litter 171
Management of Solid Waste Systems 173
Addresses of Periodical Publications Cited 189
Author Index 193
Corporate Author Index 201
Geographical Location Index 203
Subject Index 206
vi
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REGULATIONS (including Laws and
Ordinances)
65-0001
Annual report on government patent policy.
Washington, U.S. Government Printing Office,
June 1965. 13 p.
The Patent Advisory Panel was established to
develop common guidelines for implementing
the Government Patent Policy, encourage data
acquisition by agencies to serve as a basis
for policy review, and recommend uses for all
patents. The Policy contains two basic
principles. It establishes basic criteria
to guide decisions as to means of disposing
of patent rights and considers full circumstances
surrounding individual contracts or inventions.
The Panel feels that flexibility should be
implicit in any government-wide patent policy,
but the Justice Department still has not
approved this idea. Although the Policy's
effectiveness in encouraging development and
utilization of inventions cannot now be
measured, steps toward greater unity can be
reported. NASA, DOD, and AEC, agencies
responsible for approximately 90 percent of
total government R&D funds for 1964, have
published regulations implementing the
President's Policy Statement. The Panel has
issued an interpretative statement to
relevant agencies, published a Progress Report
to inform the public, collected data to
measure the agencies' patent practices prior
to issuance of the Policy Statement, and
suggested that the Secretary of Commerce
undertake a limited, experimental program for
promoting and protecting government-owned
inventions in foreign countries. The Panel
is presently engaged in reviewing agencies'
implementing regulations, considering
recommendations on the licensing of
government-owned patents in the United States,
and on the application of the Policy Statement
to university contractors and grantees.
Appendices include the President's memorandum
on stating the Government's Patent Policy and
giving a list of panel members.
65-0002
Anti-trust fines total $42,000 for Pennsylvania
contractors. Refuse Removal Journal,
8(9) :26, Sept. 1965.
Appeal was denied the Philadelphia Refuse
Removal Association and four of its officers,
who were found guilty of violating the
Sherman Anti-Trust Act. They received fines
totaling $42,500 and suspended prison sentences.
65-0003
ASCE testifies at hearings on solid wastes
disposal. Civil Engineering, 35(8):95,
Aug. 1965.
The American Society of Chemical Engineers
has submitted a statement to the House
Subcommittee on Public Health and Welfare
endorsing the Solid Waste Disposal Acts'
legislation to improve research and working
programs in solid waste disposal matters.
65-0004
Aurora moves to halt open burning. Refuse
Removal Journal, 8(9):24, Sept. 1965.
In a move to control air pollution, Aurora,
Colorado has introduced legislation to
prohibit open trash burning and backyard
incinerators. A city council study was being
made to check into the costs to homeowners
who would be required to dispose of their
own rubbish. The city's mayor stated that
private trash-hauling services in the area
charged only $1.75 a month for weekly refuse
collection. Presently, Aurora restricts
backyard burning hours to between 3 to 5 pm
and 8 to 10 pm. The Tri-County District
Health Department is attempting to get Denver
and the surrounding counties to ratify a model
air pollution control code recently endorsed
by the five-county Regional Air Pollution
Control Agency. Under the code, incineration
would be prohibited after January 1, 1968.
65-0005
Aust, A. Waste treatment in today's urban
era. Compost Science, 5(3):24-26,
Autumn-Winter 1965.
The three basic social developments in the
United States are: urbanization, technical
advances, and advances in communication. The
people are becoming more critical of obnoxious
industrial practices, and are more vocal and
insistent that corrective measures be taken
either voluntarily or by legal means. Legal
controls are: (1) planning controls, making
use of zoning and land-use control; (2) public
health controls, including advances in waste
and sewerage disposal, and in air pollution;
(3) public safety codes; and (4) aesthetic
controls, making the community beautiful,
healthy, spacious, clean, and well-balanced.
These legal developments are firmly entrenched
in the judicial processes with more to come
if industry fails to take the lead in
voluntary clean up. There are three economic
courses of action: (1) the laissez-faire or
do-nothing approach; (2) the self-sufficient
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Regulations
or self-contained approach; and (3) the
cooperative or good citizen approach. The
latter approach is the least expensive In the
long run, if this were not true there
would not be many new plants in urban areas.
65-0006
Better landfill standards, Refuse Removal
Journal, 8(11):12, Nov. 1965.
A 'totally planned" sanitation ordinance which
includes all community sectors, private and
public, is preferable to the current practice
of piecemeal legislation designed to correct
one flaw at a time. A cooperative effort
between industry and municipal officials has
provided well planned and executed regulations.
This editorial deals mainly with the upkeep
of sanitary landfill and a New Jersey ordinance
regulating bonding, liability insurance, and
fire prevention equipment.
65-0007
British Standard 3440.
55(4):188, Apr. 1965.
Public Cleansing,
British Standard no. 3440 is a basic document
for everyone involved at the executive level
in making, converting, or disposing of paper
and board. The standard puts the Council's
NEP (not easily pulpable) scheme with amendments
on an official footing, and outlines a more
practical code dealing with waste paper and
salvage.
65-0008
Buffalo mayor indicted in island dump closing.
Refuse Removal Journal, 8(9):10, Sept. 1965.
A grand jury indicted the mayor and the former
corporation counsel of Buffalo, New York, on
charges of conspiring to profit by changing
refuse disposal operations. They were
accused of closing the city-owned damps so
that the collectors could use another facility,
in which the city officials were alleged to
have been promised an interest.
65-0009
California bill wants trash bags in cars.
Refuse Removal Journal, 8(2):14, Mar. 1965.
The California State Legislature is considering
a bill to require every motorist to have a
litter bag in his automobile. This is one of
three laws introduced by State Senator Ralph
Collier as an offensive against highway
litterbugs who cost California taxpayers $3
million a year for road cleaning. Another
piece of legislation would establish a $500
fine on conviction as a litterbug. The third
bill would require a $.10 deposit on all
beverage containers in an attempt to make sure
they don't end up along state highways.
65-0010
California city makes war on illegal receptacles.
Refuse Removal Journal, 8(4):30,38, Apr. 1965.
Merced, California, has an ordinance which
enables the City's Disposal Department to
condemn improper containers. The ordinance
is reprinted.
65-0011
Chappel, W. Pass new anit-litter law.
Removal Journal, 8(4):40, Apr. 1965.
Refuse
Los Angeles passed an ordinance attempting to
clamp down on refuse haulers that litter the
streets and highways. Two major provisions
are that a city permit be obtained for each
truck used in rubbish hauling and that the
vehicles have a fully enclosed, metal body
with a cover constructed of metal or other
solid material.
65-0012
Chappel V. Stolen receptacles cause serious
fire and health dangers. Refuse Removal
Journal, 8(1):23, 28, 38, Jan. 1965.
Los Angeles County passed an ordinance which
attempts to crack down on the 'rustling' of
containers. Officials believe that some
contractors have removed their competitors'
containers, repainted and restenciled them
and reissued them among their own customers.
The stealth is regarded as a serious health
and safety hazard.
65-0013
Court ruling says municipal contract valid
without funds. Refuse Removal Journal,
8(2):4, Feb. 1965.
The right of the Township of Saddle Brook, New
Jersey, to enter into a refuse collection
contract, even though sufficient funds for a
full year's payment were not included in the
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0006-0019
current budget, was upheld in Hackensack
(New Jersey) Superior Court. The ruling ended
eight months controversy which started when
minority members of the Township Council
refused to appropriate funds for a new
collection contract. According to Judge C.
Conrad Schneider, the five-man Council had
validly entered into a 5-year contract
totaling $360,000 with Vito Stamato, Inc.
of Paramus for refuse collection. When the
minority members blocked an emergency
appropriation of $48,000 for the new contract,
there was no refuse collection for 2 weeks.
The Council majority reached an agreement with
Stamato, although full payment was not made.
The minority members then brought legal action
to have the contract declared void on the
grounds that the method of payment was not in
accordance with the published specifications,
and that the Council had no right to enter
into the contract without the necessary funds
at hand.
in all new homes. Such units would be
disadvantageous overall because they would be
a boon to rat colonies and would augment the
water pollution problem.
65-0016
Filled in land is ruled a deduction by tax
court. Refuse Removal Journal, 8(6):10,
June 1965.
The United States Tax Court has ruled that
John J. Sexton, a landfill owner in the
Chicago area, may take deductions on his
income tax for depreciation of land specifically
purchased for use in his dump operation. The
allowance is based upon the quantity of space
exhausted by filling in each year of business.
The history of excerpts from the Tax Court's
ruling are presented.
65-0014
Doose, U. Law and administration. In Refuse
and waste disposal. Berlin, Druckhaus
Lichterfeld GmbH, 1964.
Legal and administrative regulations covering
civil law, sanitation law, industrial law,
building law, water law, road law, traffic
law, and the Nature Conservation Law are
presented. Sanitation law discusses the
Federal Epidemic Law and the Cattle Plague
Law. Industrial law covers the Factory Act
of 21.6 1869/22,12.1959, Order on Licensable
Installations According to FA 4.8 1960, Law
on Protection against Air Pollution Noises
and Vibrations, and Second Ordinance for
Implementing the Immission Protection Law.
The Federal Building Law of 23.6.1960, the
State Building Codes, the Regulations
governing installations for solids waste, the
Regulations for Waste Chutes, and ARGEBAU
Standards for the Construction of Waste Chute
and Incineration Installations are discussed
under Building Law. The Water Conservation
Law of 27.7 1957 and the Water Protection,
Administrative Measures on Road Tanker Accidents
and Leakage in cases of Mineral Oil are
presented.
65-0017
Forty million dollar Senate waste bill would
grant sums for research. Refuse Removal
Journal, 8(7):20, July 1965.
The U.S. Senate has passed a 2-year $40-million
bill that would amend the Clean Air Act and
set up a Solid Waste Disposal Act. Under the
bill, the Department of Health, Education,
and Welfare would conduct, encourage, assist,
and finance projects on solid waste disposal.
65-0018
Garner, J. F. Discussion of 'The law and
public cleansing'. Public Cleansing,
55(8):469-473, Aug. 1965.
Answers to legal questions posed after the
above talk regarding collection sites,
material which should be collected, definition
of household refuse, and other questions on
refuse collection associated with British
law are discussed. Lack of laws committing
municipal governments to fully hygienic and
satisfactory service was noted. Salvage days
on premises are considered.
650015
An editorial.
8(2):14, Feb.
Refuse Removal Journal,
1965.
A national plumbers association is campaigning
to promote the enactment of a city ordinance
requiring the use of food waste disposal units
65-0019
Hope, M. C. Solid waste legislation. Journal
of Environmental Health, 28(2) : 123-126 , Sept.-Oct.
1965.
The recent federal legislation in the disposal
of solid wastes is discussed. As various
national organizations emphasized, proper
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Regulations
solid waste disposal is vital to public health
and to environmental beauty. Upon the
President's recommendation for legislation, the
Administration drafted a bill to assist states,
communities, and industries in prevention
and control of solid waste problems at a $10
million level for the first year. The bill
encouraged interstate and interlocal cooperation,
and made grants to state and interstate
agencies not to exceed 50 percent of the
survey costs of disposal practices and plans.
Also included was authorization for a
national program of research and demonstration
projects. The Secretary of Health, Education,
and Welfare was designated to administer the
act. Secondly, a new S.306, Title II bill
was proposed, similar to the Administration
bill, although somewhat more restrictive. It
authorized the following grants-in-aid: for
research, up to 25 percent of the total
amount appropriated for any fiscal year; for
demonstration projects, up to 2/3 of the cost,
under specified provisions; for surveys, up
to 2/3 of the cost. Appropriations authorized
for fiscal years 1966 and 1967 were $20
million per year to remain available until
expended. Finally, the House proposed H.R.
890, also similar in purpose to the preceding
two bills, with particular emphasis on
facilitating advanced types of processes or
practices. In addition it authorizes grants
to states at a level of $2 million for 4
years for development of state programs. This
act would be administered by the Surgeon
General.
650020
The law and public cleansing. Surveyor and
Municipal Engineer, 125(3812):35b-36, June
26, 1965.
A discussion of a paper given by Professor
Garner, concerned with legal definitions of
the various types of refuse which have to be
collected by the local authorities and the
conditions under which refuse has to be
collected, is reviewed. The law covering
the work of a public cleansing department
is largely permissive and describes the
refuse and materials which have to be collected
stressing the point that trade wastes are
recognized by their nature and not by the
premises from which they arise. Some fine
legal distinctions were made in that a
caravan is not a premise, but the site upon
which the caravans stand is considered a
premise. A paper sack may be considered to
be a dust bin, but not the sack holder. The
local authority must show the Court a
reasonable excuse for non-collection of
refuse. The fact that vehicles were not
available for collection was not considered
a reasonable excuse nor was the failure to
place the dustbin in a position that the local
authority thought proper. A strike could be
considered a reasonable excuse for the
non-collection. No powers were granted to
put bins on the highway and it was questionable
if the local authorities could require the
householder to place a bin at the curb for
collection. The question was raised as
to the requirement that domestic refuse be
placed in a container and whether this would
rule out an old chair or a settee as domestic
refuse. The decision was, that if the bulky
items were lying beside the bin they must be
collected. Several definitions were
unavailable, such as 'trade refuse'.
65-0021
Liner fined $250 for coastal dumping. Refuse
Removal Journal, 8(2)-.26, Feb. 1965.
The Justice Department fined the Cunard
Steamship Line $250 for littering by its
liner Caronia off the New Jersey shore. The
company still faces possible legal action by
the State of New Jersey.
65-0022
MacKenzie, V. G., and K. Flieger. The Clean
Air Act amendments and Solid Waste Disposal
Act of 1965 (P.L. 89-272). Health, Education,
and Welfare Indicators, 1-13, Nov. 1965.
On October 20, 1965, President Johnson signed
P. L. 89-272 which amended the Clean Air Act
of 1963 and brought into being the Solid
Waste Disposal Act. The Clean Air Amendments
give the Secretary of Health, Education, and
Welfare authority to control air pollution
from new motor vehicles, take action to abate
air pollution from endangering neighboring
countries, seek methods to prevent new sources
of air pollution, and expand the Department's
facilities to meet these new responsibilities.
The Solid Waste Disposal Act enables the
Federal Government to help create a coordinated
national solid waste disposal program by
bolstering the efforts of state and local
governments. It authorizes two basic kinds
of activity, training and research and grant
support for demonstrations and planning
of local and state programs. These grants
stimulate state, local, and regional agencies
to develop and operate disposal systems that
are sanitary, efficient, and economical.
This act appropriates more than $92 million
over the four fiscal years of 1966 to 1969
for the Department of Health, Education, and
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0020-0028
Welfare and the Department of Interior.
The goal of the act is to reverse the present
trend in waste disposal and promote more
desirable methods. Additional data,
illustrations, and comments are included.
(Reprint)
65-0023
Measures taken to ban bootleg burning at
dumping areas. Refuse Removal Journal,
8(1):4, Jan. 1965.
New Jersey has begun a drive to stamp out
illegal burning at refuse dumping grounds in
the North Jersey Meadows. The State had
outlawed open dump burning in 1958.
650024
Municipal liability for burning of garbage.
Public Works, 96(8):180, Aug. 1965.
In City of Purcell v, Hubbard, an Oklahoma
court ruled that the city was not liable when
a fire in an open burning dump spread to the
plaintiff's land. The city was immune because
the collection and disposal of garbage was
held to be a governmental function.
65-0025
New Jersey group urges state study land
leasing practices. Refuse Removal Journal,
8(9):25, Sept. 1965.
The East Orange, New Jersey Council is
considering a resolution demanding a State
investigation into practices of leasing
northern New Jersey meadowlands to refuse
contractors. The resolution was prompted by
the failure of an association of seven New
Jersey towns, including East Orange, to lease
a disposal site.
65-0026
Roosevelt, J. Solid waste bill to provide
43 million dollars. Refuse Removal Journal,
8(5):16-17, 30, 34, May 1965.
The speech by Rep. James Roosevelt (D-Cal,),
who argues before the House for the adoption
of the Solid Wastes Disposal Act of 1965 is
reprinted. The act provides $43.6 million
for research. The problems of solid waste
disposal throughout the ages are described
with emphasis on today and possible solutions
to the current problems are briefly related.
650027
St. Joseph seeks lot clean-up law. Refuse
Removal Journal, 8(1):29, Jan. 1965.
The city of St. Joseph, Missouri, is seeking
legislation requiring the removal of automobiles
abandoned on vacant lots, as well as other
debris. The bill now pending before the
Board of Aldermen will make it mandatory that
private property owners keep their vacant areas
clear. Upon violation of this, the city would
be authorized to go onto the property and
remove the debris and abandoned automobiles.
The cost of the removal and disposal would be
assessed against the owner as a tax lien, if
he refused to clean ii.e land or repay the city
for doing it. According to Robert W. Duffe,
Director of Public Safety, the derelict autos
are abandoned on vacant lots in many parts of
the city, and at some spots additional
derelicts appear almost as fast as old ones
are towed away. He stated that the city now
has the authority to remove them from the street,
but needs the authority to remove or require
their removal from private property.
65-0028
Association news: Solid waste disposal.
American Journal of Public Health and the
Nation's Health, 55(12):2006-2007 , Dec. 1965.
The American Public Health Association
recommends federal legislation to assist in
solving the problem of solid waste disposal
which faces every city and metropolitan area
in the United States. The improper storage,
collection, and disposal of garbage, rubbish,
and refuse, increases the problem of
controlling the insect and rodent vectors of
disease as well as atmospheric and water
pollution. Federal and State programs of
expanded research, demonstration, and
training are needed to develop satisfactory
methods of solid waste storage, collection,
transportation, processing, and disposal.
The American Public Health Association urges
the passage of federal legislation to
provide for: (1) an enlarged and accelerated
research program for improved and economical
methods of storing, collecting, processing,
and disposing of solid wastes; (2) technical
assistance to State, metropolitan and
local governments in planning, development,
and conduct of improved solid waste disposal
programs; and (3) financial assistance to aid
in the establishment of demonstration projects
and training of professional personnel in
methods of improved solid waste disposal
programs. The State and local health agencies
should work with and promote coordination
among public works, sanitation, and other
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Finances
agencies to assure safe, sanitary, and
aesthetically acceptable methods for the
collection and disposal of solid wastes.
FINANCES (including Costs. Fees, Taxes,
etc.)
65-0029
Solid waste programs. Refuse Removal Journal,
8(12) -.20-21 , 34, Dec. 1965.
Provisions and aims of the Solid Waste Act of
1965 are described. Presently only $5 million
a year are spent on solid waste research. This
act authorizes up to $60.2 million over the
next 3 years to be spent on research, training,
experiments and studies to find and apply new
solutions to waste disposal problems. The
provision and machinery of this act are
explained briefly.
65-0030
Vehicles classified by materials hauled.
Refuse Removal Journal, 8(2):22, Feb. 1965.
The Sanitation Department of New York City
classifies vehicle bodies by the types of
materials carried to promote public health
and prevent the littering of streets. Depending
upon the assigned category, extra license or
permits are issued. The six classes are:
Class 1: transportation of garbage or rubbish
(license); Class 2: transportation of ashed
or manure (license); Class 3: transportation
of materials (other than manure and those in
classes 4, 5, 6) originated and produced
solely in the business operations of the owner
of the vehicle (permit); Class 4: transportation
of dead animals, non-edible fats, bones,
greases, and other refuse parts of animals, raw
hides, or uncrued skins (permit); Class 5:
transportation of contents of cesspools, septic
tanks, sinks, privies or vaults, and of
other noxious or contaminated or polluted
liquids (license); Class 6: transportation of
swill (license).
65-0031
What federal aid means. Refuse Removal
Journal, 8(12):12, Dec. 1965.
Results of the Solid Waste Disposal Act of
1965 are anticipated. More efficient, lower
cost disposal, testing of various collecting
equipment and long distance disposal systems,
and stimulation of private disposal concerns
to improve products are projected.
65-0032
Carozza, M. J. Contract negotiations result
in ... prudent equipment purchasing. American
City, 80(10):107, 148, Oct. 1965.
The procedure on which Fresno, California,
bases its equipment purchases is described.
The method requires three steps: (1)
inventory analysis; (2) cost and performance
analysis; and (3) market analysis. The
practical application of this approach was
illustrated by the purchase of 20 new
packer-type disposal trucks. Using the
above-mentioned criteria, the City decided on
a lease-purchase arrangement. The contract
runs for 5 years, and the City has the option
to purchase these units at the end of 5 years
at 20 percent of the market value at the time
of delivery. The Disposal Division makes
double payments to cover this cost. Lease
payments go to the local bank, and
depreciation payments are placed in an
equipment-replacement fund.
65-0033
An editorial.
May 1965.
Refuse Removal Journal 8(5):12,
Ways of meeting rising costs of refuse
collection, including research, the use of
latest equipment, expansion of business, and
greater efficiency are discussed. Cutting
rates are dismissed as unworkable.
65-0034
Eppig, T. C. Refuse collection truck purchase
includes guaranteed maintenance program.
Public Works, 96(8):98, Aug. 1965.
The 'total cost' of collection trucks is
being taken into account in the bidding for
the city of Chicago contracts. Contracting
companies are expected to provide a guaranteed
maintenance program for the anticipated useful
life of each truck. Several specifications are
cited and one conclusion seems to be that the
success of this program is largely dependent
upon the good will of both the contractor and
the city.
65-0035
Equipment bids must have guaranteed maintenance.
Refuse Removal Journal, 8(1):18-19, 25, 28,
Jan. 1965.
6
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0029-0040
Chicago now requires equipment suppliers to
submit maintenance contract bids, in addition
to their regular equipment bids. The first
contract under the new bid system was won by
the White Motor Co., which will provide
complete maintenance for 6 years of 75 of the
100 refuse collection trucks it agreed to
sell the city. Chicago has to pay $218 per
month per vehicle for the maintenance bid,
which contrasts with the previous monthly
maintenance average of $293. (The contract
is included in full.) Chicago also signed a
similar agreement for a tractor dozer for a
landfill site.
65-0036
Fales, J., J. Gardner, and H. Peyser. Do
trash collection dollars steal away in the
night9 Part I. Modern Sanitation and
Building Maintenance, 17(7):36, 19-21,
July 1965.
The staff at Columbia University found that
20.2 percent of janitorial payroll was spent
on trash collection. Time was wasted by
constant transferring from one container
to another. Trash came in contact with
workers, making the job unsanitary and
distasteful. They decided the ideal system
would be a disposal unit in each desk which
pulverizes trash and pipes it into the sewer
system. As this is too costly, they decided
to have disposable plastic bags line all
containers. This eliminates washing containers
and personal contact with garbage. Offensive
odors are sealed off. Time is reduced. They
are converting one floor at a time. All waste
baskets are washed. The maid is given a
supply of plastic bags. The first maid
converted showed a 22 percent improvement.
65-0037
Fales, J. T., and J. C. Gardner. Do trash
collection dollars steal away in the night?
Part II. Modern Sanitation and Building
Maintenance, 17(10):24-25, Oct. 1965.
The trash filled plastic liners are dropped
into large plastic bags attached to the maids'
carts. When the large plastic bags are filled,
they are sealed and placed near the elevator.
The janitor collects the filled bags and puts
them on a cart. One typical maid had almost
a 50 percent reduction in labor. Use of the
liners is a more economical method of
collection although the plastic bags cost
more. Maids can increase the amount of floor
space they can handle. The occupants of the
Law School at Columbia University like this
system.
65-0038
Moschell, R. V. Sell tickets for extra
collections. American City, 80(9):18,
Sept. 1965.
In the past, residents of Middletown, Ohio,
were billed individually for special pick-ups,
when they exceeded their allowance of AO gal
of refuse per week. The customer had to call
for pick-up; a truck was dispatched and the
customer was billed. This unwieldy and
costly method was replaced by a new system.
Residents can purchase tickets in strips of
ten for $2 (just $0.20 each), and attach one
ticket to each 20 gal can. The extra refuse
is then picked up during regular collection
days. If they prefer, residents can haul their
extra refuse to the city's landfill. The
new service does not include yard rubbish
which the city collects without charge between
April 2 and September 30, if placed at the curb
on regular collection days.
65-0039
Report on waste disposal. Wasser und Abwasser,
106(36) .-999, Sept. 10, 1965.
Upon request of the Federal Ministry of
Health, Prof. Gerlach, Berlin, worked out an
extensive report on 'cost analysis and
investigations of economy of the various
different methods for the removal of
municipal wastes'. In great detail he deals
with the known methods of waste disposal and
discusses their economy. Part I of this
report appears as number 7 of the series
'Deutscher Arbeitskreis Wasserforschung',
Duesseldorf, published at Verlag Erich Schmidt,
Berlin. Part II describes 66 plants and
provides extensive data. Only a limited
number of copies are available at:
Deutscher Arbeitskreis Wasserforschung, 4
Duesseldorf, Rosenstrasse 66. (Text-German)
650040
Shuval, H. I. Economic aspects of composting
in Israel. Public Cleansing, 55(3):155-157,
Mar. 1965.
The economics and market for compost in
Israel are outlined. A brief description of
Haifa's 50 ton per day plant and Tel Aviv's
50 ton per day pilot plant for the 500 ton
per day plant under construction there is
given. Because Israel has been intensively
farmed for centuries, organic fertilizers are
in great demand. Prices of $2 to $5 per cu m
(about a ton) are paid for different grade
composts, the higher grades being the most in
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demand. The municipalities presently subsidize
the operations at Haifa and Tel Aviv by $0.60
per ton and $1.20 per ton respectively, which
is cheaper than other sanitary disposal
methods. It was estimated that should all of
Israel's refuse be composted, only one-half of
the country's need could be met.
65-0041
Sludge-incineration costs.
80(6):16, June 1965.
American City,
It is suggested that cost data on sewage
treatment include incineration of sewage
sludge. The ultimate disposal of sludge is
becoming more important as urban land becomes
more valuable and water pollution must be
avoided. For most communities, incineration
is the most economical disposal method.
Multiple-hearth incineration equipment
is free of air pollution and odor problems so
that incineration is aesthetically acceptable
in any community. An accompanying table
gives approximate system and annual operation
costs using the B-S-P Multiple Hearth Incinerator,
according to size of the community. Both
first and operating costs of vacuum filtration
and conditioning chemicals are included.
wastes and industrial refuse; (2) standard
plants processing residential refuse, bulky
wastes and industrial refuse, operating on
an assembly line basis; and (3) complete
plants for all wastes except inert material.
In calculating operating costs, power use,
water use, and maintenance and repairs are
considered. An attempt is made to find the
relationship between the population density,
the regional area and the average hauling
distance, and to check the results by means
of a practical example. The average hauling
distance of all routes Is a factor for the
over-all economy of the arrangement. The
data show that, with a Type 1 plant, acceptable
economy could be attained for 50,000 residents,
while, with complete treatment in a Type 2
plant, savings seem very possible even with
the enlargement of the region to over 100,000
residents. With a greater density of population
or higher per capita yield, the characteristics
will change so that appropriate treatment
costs must be added to the smaller hauling
costs,
STORAGE (including Methods and
Equipment)
65-0042
Take measures to cut equipment downtime.
Removal Journal, 8(10): 16, Oct. 1965.
Refuse
Sixty percent of every dollar spent for labor
goes toward upkeep, but about 35 percent of
this total is 'comeback' work. Factors which
contribute to 'comeback' work are listed.
Some steps that should be taken to reduce
costly maintenance are keeping a record of
all equipment and proper purchasing and
planning.
65-0044
Cans banished from paper-making city.
Removal Journal, 8(1):14, Jan. 1965.
Refuse
The industry of Dryden, Ontario, is paper-making
and the town has forbidden the use of refuse
cans or any receptacle except a special paper
sack known as a Refubag, as enforced by a
special bylaw passed recently by the Town
Council. Dryden is thought to be the first
community in Canada to take this action.
Wallaceburg, Ontario, is expected to follow
suit.
65-0043
Wuhrmann, K. Which method for rural
areas--incineration or composting? Compost
Science, 1(6): 16-1 8, Spring 1965.
The safe disposal of residential and industrial
refuse is discussed from an economic point of
view. Construction and annual operating cost
for a city of 100,000 is about twice as high
per capita as it is for a large metropolis.
There is a demand for centralization and joint
construction. The operating costs for the
following three types of refuse plants are
compared: (1) simple plants processing
only residential refuse and part of the bulky
65-0045
Complaints came with the frost. Public
Cleansing 55(10):582, Oct. 1965.
East Kilbride, Scotland, has disclaimed
responsibility for plastic dustbins cracked
during emptying in very cold weather.
Complainees were recommended to use a metal
dustbin.
65-0046
Container for flammable waste.
46(4):W42, Apr. 1965.
Brennstoff-Chemia,
8
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0041-0051
A container for flammable waste is now
commercially available. It is made of sheet
steel; its dimensions are 40 by 40 by 73 cm.
The lid closes automatically, thereby putting
out any fire which may arise in the container.
Painted red, it is suitable for oil or
gasoline soaked cloths and other easily
flammable material. (Text-German)
The two British towns of Whickham and
Blaydon with about 3,000 homes each have
adopted a paper sack collection system. High
population growth rate, and changes in
housing developments from compact homes with
alleyways to developments with long walks or
on hillsides were factors in the change.
65-0047
Containers for household refuse.
Works, 96(5):82, 84 May 1965.
Public
A questionnaire was mailed to a group of
600 health officers and sanitarians by the
Public Relations Department of the Galvanized
Ware Manufacturers Council. The purpose
was to determine reactions to containers for
household refuse. Replies were received from
234 (39%); some 220 of the 234 said that
covered containers are a major factor in
controlling rats, flies and disease; 86
percent of the respondents felt that metal
cans were the best home system for handling
refuse; 34.6 percent combined such containers
with food waste disposers as the best system;
and another 10 percent combined metal cans
with home incinerators. Metal containers were
preferred by 98.7 percent. About 30 percent
of the cities in the country lack safe cans
in more than half of the places where they
are needed. This lack was not confined to
any particular area or size of city.
65-0048
Davies, A. G. Why Blaydon introduced paper
sacks. Public Cleansing, 55(4):221-222 ,
Apr. 1965.
Due to hilly terrain and residential estates
which involved long carrying distance of refuse,
the Blaydon Council of Great Britain resolved
adoption of paper sack containers. Since the
sacks have been used, less physical work is
required and work is cleaner and quieter. It
previously took two men 45 minutes to clear
twenty bins; now one man can clear twenty
sacks in 5 minutes. During severe winter
weather, isolated farm communities did not
receive refuse collection. Now the
communities receive a supply of sacks which
can seal the refuse inside. No nuisance
occurs. The sacks are collected when weather
permits. The sacks are stable under all
conditions, and economical.
65-0049
Development of paper sacks in the North East.
Public Cleansing, 55(9):533-534, Sept. 1965.
65-0050
Dutton, D., and C. Wood. Waterloo, Ont. test
plastic bags for refuse collection, APWA
[American Public Works Association] Reporter,
32(5):3, 13, 14, May 1965.
A pilot run of one pick-up for 40 houses
resulted in favorable reactions and a
programmed main test in Waterloo, Canada, a
city of 26,000 with once-weekly residential
refuse collection. The main test included
563 houses but no commercial or industrial
buildings. The 30 by 40 in. bags were
manufactured by F. G. Plomp Co., Toronto, from
1*4 ml polyethylene film supplied by W.
Ralston & Co., Ltd., Rexdale, Canada. The
plastic is green and semi-opaque. Bags were
used as liners in regular metal containers
with the top folded over the edge. Bags are
tied at the top when full and placed as
usual at the curb. Generally a driver and
one helper could handle the collection, instead
of two helpers now employed. At about 20
percent of the stops, other containers were
put out for collection, generally for ashes
and other items such as newspapers, yard
wastes, and bottles. Many bags went through
the packer mechanism without breaking up, but
there was no problem at the landfill. One
hundred and twelve householders were asked
for reactions if they had to purchase bags
at 10 to 15 cents each and 69 said 'yes';
10 percent said 'no' and 21 percent were
undecided. Some said the bags tore when
they were picked up and the manufacturer
suggested a smaller bag of \\ ml thickness.
This would cost 8 for $1.00 in local stores.
If a metal holder is used, a 2 ml bag will
be required at a cost of 6 for $1.00. Large
quantities of bags can be obtained at about
$5.72 each and they can be distributed for
$6.49 each for a 3 months' supply. While labor
costs might be decreased as much as $13,316 per
year, collection costs would increase by
about $27,172 if the city provided and
distributed the bags.
65-0051
Ecke, D. H., D. D. Linsdale, K. E. White, et al.
Green blow fly studies in Saratoga, California.
California Department of Public Health, Bureau
of Vector Control, 1965. 17 p.
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A multiple comparison rank test was made of
fly larval migrations from 222 garbage
containers of six different types to determine
their comparative value in reducing green
blow fly larval migration. The following six
systems were studied: metal cans with
once-a-week collection, metal cans with
twice-a-week collection, Vapona strips in
metal cans with once-a-week collection, an
exposed paper bag with once-a-week collection,
an enclosed paper bag with once-a-week
collection, and a liner bag with once-a-week
garbage collection. The liner bag system
showed no statistically significant: improvement
over once-a-week garbage can service.
Twice-a-week can service, Vapona treated
garbage cans, and two systems of suspended
paper bags all showed significant improvements
over the once-a-week garbage can system. No
significant differences were demonstrated
between systems in the improved group. None
of the systems accomplished total elimination
of larval migration even though four showed
significantly less migration. No suitable
device has been developed by which the
Vapona strips can be readily fastened to
garbage can lids. The method of adult fly
sampling consisted of establishing sampling
stations, located in the sun within 3 ft of
garbage cans at ground level. Open cans of
dog food were exposed for 10 minutes while
one observer watched the time and the other
recorded the maximum number of Fhaenicia
which landed.
65-0053
Ecke, D. H. Study finds paper sacks cut fly
nuisance. Refuse Removal Journal 8(12) :6, 30,
35, Dec. 1965.
Results of six mixed refuse storage and
collection systems with regard to fly control
are compared. The systems included cans
(once- and twice-weekly collections) , cans
with Vapona strips attached to the underside
of the lids, supported sacks, enclosed sacks,
and exposed sacks. Great care was taken to
equalize variables which could alter or
prejudice data in favor of one system or
another. Results of the study are analyzed
in tables which show that fly larval migration
during the 10 weeks of study was greatly
reduced in exposed sacks, enclosed sacks, and
Vapona cans. Community-wide use of the
exposed and enclosed sack units should
effectively repress the adult fly population
below the pest level. Such a test is being
planned in part of Santa Clara County during
the summer of 1966.
65-0054
An editorial. Refuse Removal Journal, 8(3):14,
Mar. 1965.
The use of detachable containers has grown
1,600 percent since 1958. The new stationary
packer is so far in the front rank of
containerization. Contractors are urged
to keep up with the trend by pushing
containerization.
65-0052
Ecke, D. H., D. D. Linsdale, and K. E. White.
Migration of green blow fly larvae from six
refuse container system. California Vector
Views, 12(8):35-42, Aug. 1965.
Fly larvae production in 6 garbage and storage
systems from a study involving 240 residents
operating 40 of each system over a period of
10 weeks in Saratoga, California is reported.
The methods include weekly cans, Vapona
insecticidal lidded cans, weekly exposed
freely-suspended paper bags, weekly enclosed
suspended bags, and weekly metal-container
supported bag liners. Selection of residences,
data collecting, and statistical analysis of
the study are explained. The results showed
significant and approximately equal decrease
in the twice-weekly cans, Vapona, exposed bags
and enclosed bags systems, but no improvement
over weekly cans by using the bag-liner system.
Community-wide tests will be necessary for
more thorough analysis of these systems.
65-0055
400 year old Florida city modernizes with
containers. Refuse Removal Journal, 8(1):16,
22, Jan. 1965.
St. Augustine, Florida, the oldest city in the
United States, recently added 90 containers
for use by the business establishments. The
city's narrow alleys and streets pose
transportation problems for the modern trucks.
The city owns a landfill site. The city
employs 17 men to collect the trash and has a
safety program, whereby the employees meet
once a month to discuss the nature and causes
of accidents and injuries.
65-0056
Half of Sweden uses paper sacks. American
City, 80(6)-.61 , June 1965.
After 13 years, more than one-half of Sweden's
communities are either using or testing paper
10
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0052-0062
bag refuse collection. Replacing noisy and
unsatisfactory garbage cans with paper sacks
is much newer in the United States. Two cities
doing so have favorable reports of acceptability
and satisfaction. They like the lack of noise,
odors, and spillage. There is little cost
advantage though collection is faster.
65-0057
Hospital x plastic liners = greater efficiency.
Modern Sanitation and Building Maintenance,
17(5) .'21-22, May 1965.
The housekeeper of a New Jersey hospital found
that polyethylene liners cut work and improve
sanitation. Before, janitors had to
steam-clean swivel cans and waste baskets.
Now the janitor picks up the liners and puts
them into castered swivel cans which also
have liners. The large liners are tied to
seal off contents until burned in the
incinerator.
65-0058
How paper made College Park, Maryland, a
cleaner city overnight. New York, West
Virginia Pulp & Paper Company, 1965.
27 p.
The Council and City administrator of
College Park, Maryland, were seeking a
cleaner, quieter, and more economical system
of refuse removal. College Park officials
were invited to witness a test operation of
the Westvaco Papercan Bag System, which uses
heavy-duty paper bags in place of garbage cans.
A detailed field test of the system in operation
was initiated in College Park in order to
study its adaptability to the City's needs,
requirements, and budget. A time study,
financial review, and controlled test of the
system were made. The two-month test proved
the System's superiority in service, manpower,
equipment, and cost. Homeowner approval
was overwhelming, and the system was adopted
in College Park in July 1962, with an
ordinance made effective January 1, 1963.
The city bore the basic cost of putting
the program into effect, providing each
homeowner with one wall holder and two Papercan
bags per week. Six months later, the
Westvaco Papercan Bag System was adopted in
nearby Riverdale, Maryland. Charts of test
results are included, and an evaluation and
analysis by the Superintendent of Public Works
is given.
65-0059
The Irish Capital gets containers. Refuse
Removal Journal, 8(11):26-27, Nov. 1965.
A containerized industrial waste operation
has been initiated in Dublin. Advantages
include labor efficiency sanitation in a
highly agricultural country, and neatness
for the tourist. A sanitary landfill is being
used to reclaim commercial lands from Dublin
Bay.
65-0060
New hardware. Engineer, 199(5156):224,
Feb. 12, 1965.
The Hardware Trades Fair, held annually at
Olympia, which introduces retailers to
manufacturers' new products is described. An
example of the increased willingness of
designers to study new user needs in 'peripheral'
products is the 'Ericol' kitchen waste
disposal cabinet. A disoosable bag is housed
within the waste hopper and since no waste
touches the cabinet, cleaning out is
unnecessary. The lining hag is sealed when
full with a tie strip which is provided and
dustbin cleanliness is assured. Another
item mentioned is a vacuum cleaner without a
dustbag. The two-wheeled body is up-ended
for emptying, two toggle clamps are released,
and the wheeled motor unit is lifted off.
A conical fabric filter element is removed
and the remainder of the case can be easily
emptied. A 6 ft suction hose is provided,
together with a selection of cleaning tools.
The motor is rated at 450 W.
65-0061
Paper bags for waste disposal save hospital
money. Modern Sanitation and Building
Maintenance, 17(2):19-21, Feh. 1965.
A Pennsylvania hospital uses bags of double-ply
Kraft paper used in sizes ranging from 36 to
58 gal capacity. They are fully enclosed in
fire-proof containers while in use. Odors
are sealed in; flies and pests, sealed out.
There is no chance of spillage. The bag is
slipped through the front where a hinged panel
can be dropped down. The bag is stapled and
loaded onto a cart for transfer to a compressing
bin.
65-0062
Paper refuse sacks aid land-fill. Modern
Sanitation and Building Maintenance, 17(9):30,
Sept. 1965.
11
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Storage
A year long test in Manchester, England, showed
that polythene sacks slowed down the normal
rate of decomposition of refuse contained in
the sacks while refuse in paper sacks
decomposes faster and is better for sanitary
landfills.
Refuse collection companies are the greatest
users of paper sacks in Sweden. Thirty-three
gal sacks are the most commonly used. In
some large apartment houses, a paper bag
compaction machine is employed.
65-0063
Paper sack unit packs and compresses at site.
Refuse Removal Journal, 8(2):22, Feb. 1965.
Designed for commercial and industrial use,
the Deva refuse compression system
automatically compresses and packs waste
material into on-site disposable paper sacks.
Six models are being manufactured by a
British firm.
650064
Paper sacks cut fly larval production.
American City, 80(11):44, Nov. 1965.
A 10 week test conducted by the California
Health Department showed that paper sack
refuse containers reduced larval production
to almost that of twice-a-week collection of
cans. The test included the use of 30 gal
metal cans collected once a week and twice a
week, 30 gal metal cans with Vapona strips
attached to the underside of the can lids,
exposed sacks, enclosed sacks, and liner sacks
collected once a week. The exposed sacks
were freely suspended from holders, while
the enclosed sacks were enclosed in
rectangular metal containers. The liner
sacks were placed inside regular metal
containers. All units rested on rectangular
maggot traps designed to capture fly larvae
as they migrated from the refuse containers.
A table summarizes the total, average, and
median production of fly maggots during the
test. Total larvae count for once-a-week
cans was 249,927; for liner sacks, 150,905;
for Vapona 32,793; for enclosed sacks, 38,399;
for exoosed sacks, 16,200; and for
twice-a-week cans, 23,786. Although minor
differences existed between the Vapona, exposed
sacks, enclosed sacks and twice-a-week cans,
these differences were considered not
significant in view of the wide variability
of the data.
65-0066
Refuse sacks are in. American City,
80(12):96-97, Dec. 1965.
Mt. Wolf, Pennsylvania, uses the St. Regis
Refuse Sack System in lieu of conventional
garbage cans. The refuse sacks eliminated
the wide variety of miscellaneous unsightly
and odorous containers which were placed on
the sidewalk the night before collection day
where they were disturbed by dogs and
attracted maggots and insects. Once the
refuse sacks were adopted by the Borough
Council, sacks, holders and a year's supply
of St. Regis Refuse Sacks were distributed to
all homes, but remained the property of the
borough. Each sack holds about the same
volume as one and one-half normal garbage cans
(30 gal); 36,000 bags were distributed
throughout the community. Although there
were some initial complaints, the people
cooperated when they found that their garbage
was not being collected if it was not in the
sack. The fly population has diminished, and
stray dogs leave the sacks along when closed
properly. The collection operation is
completed in 4 hr instead of 8 and less
work is involved as each sack weighs only ->>
Ib as compared to approximately 5 Ib for the
average garbage can. Less time is involved
as the sacks are carried only once to the
truck, whereas the cans had to be returned to
the sidewalk.
65-0067
Sacks quiet apartment pickups.
Journal, 8(5):6-7, May 1965.
Refuse Removal
New York City's Big Six Towers, a row of
apartments in Queens, now stores its refuse
in paper bags. This system eliminates noise,
spillage on the streets, and contact with refuse
and its fumes by the collectors. The paper
bags, which save $5,000 a year in refuse
handling, can also be carried much more
easily up and down flights of stairs.
Previously the apartments used 30-gal metal
cans.
65-0065
Rasch, S. Refuse service is greatest user
of bags in Sweden. Refuse Removal Journal,
8(10):23, 32, Oct. 1965.
65-0068
Sacks solve their problems.
55(6) :336-337, June 1965.
Public Cleansing,
12
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0063-0073
Kirkburton, England, a town with 5,000 homes,
is changing to a paper sack collection system.
With one-half of the homes now using paper
sack wall bracket or wire mesh holderr.
collection in these areas has increased from
10 day to weekly service. The work is more
pleasant and lighter for employees. The new
system has already brought a profit account to
the city.
showed waste in paper sacks allowed normal
decomposition, but polyethylene bags preserved
the waste.
COLLECTION AND DISPOSAL-General
65-0069
Sanborn, K. F. Garbage cans' Who needs them?
Public Works, 96(3):148,150 , Mar. 1965.
Municipal garbage collection crews serve
about 50 percent of the population of
Junction City, Kansas. Six private contractors
serve the remainder. Municipal customers,
identified by a card system, receive
twice-a-week service using the carry-out
method at a cost of $1.25 a month. Compactor
trucks on three regular routes serve 2,910
single unit dwellings and 430 multiple units.
The main problem was the use of unsanitary,
unsafe, and improperly maintained refuse
containers. They decided to use the Westvaco
refuse system which employs heavy-duty
disposable bags hung from metal holders. The
bags are manufactured from stretchable kraft
paper, treated with wet-strength resins to
make it weather-proof and leak resistant. A
250-home pilot study was conducted in July
to August 1963. Participating residents were
given questionnaires. Of those answering, 88
percent liked the system; 85 percent felt
that the bags were more sanitary than metal
containers; and 75 percent favored adoption
by the city. Paper bags permitted an increase
in the number of collections per crew member
and decreased daily trips to the landfill
from four to two per truck. The presence of
a bag holder readily Identified a city
customer, eliminating the expense of the card
identification system. In January 1964, they
offered residents the 'Deluxe City Service' of
two bags per week plus holder and lid, charging
them a total of $1.75 per month, $0.50 per
month more than for conventional services.
After four months, about 23 percent of the
city's customers were receiving the new deluxe
service.
65-0070
Study finds sacks decompose at same rate as
contents. Refuse Removal Journal, 8(11):42,
Nov. 1965.
One year test of polyethylene bags and paper
sacks in a landfill in Manchester, England,
65-0071
The application of plastics in public cleansing.
Public Cleansing, 55(8):451-458 , Aug. 1965.
Plastics seem entirely suited as a material for
bins, skeps, and Utter receptacles, but no
satisfactory product has been shown yet.
Polypropylene is a low-cost plastic efficient
through a wide temperature range, but most
have prohibitive costs. Various other
problems with plastic sacks are discussed,
including the production of black smoke during
tipping. There was a question as to the
durability of the plastic bins, their weight,
tip drainage, and incineration. Linings and
coatings for the bins was also discussed.
65-0072
Archer, G. A. Discussion of 'Mechanical
Refuse Disposal'. Public Cleansing,
55(8):458-464, Aug. 1965.
Comments were directed at points concerning
the use of refuse volume rather than weight
in disposal plant design and in collection
facilities. A close alliance between
collection and disposal authorities, and the
need for a correct and overall analysis of
refuse on a non-seasonal basis, with
projections of the refuse nature in the
future were discussed. The use of steel
frame plants to facilitate expansion, and
the dubious financial advantage of pulverizing
before incineration were also mentioned.
Advantages of the grab hook over the conveyor
for refuse storage and movement were presented.
No difficulties in mechanical grate operation
from slag formation were reported.
650073
Black, R. J. President Johnson spurs nation
to act on solid waste problems. Refuse
Removal Journal, 8(7) :8, July 1965.
A growing public interest in the environment
is reported. A general survey of the front
rank of refuse handling and disposal, including
health, aesthetics, and economical requirements
13
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Collection and Disposal General
is reported. California has contracted a
firm to develop a detailed and long range plan
for a state-wide management system. North
Tonawanda, New York, is automating sanitary
landfilling with a new machine, which
simultaneously digs a trench and buries the
refuse.
65-0074
City of Reading. Your plan for community
improvement. City of Reading environmental
sanitation survey. 1964. 14 p.
A sanitation survey was undertaken to determine
the nature and magnitude of the environmental
sanitation problems in Reading, to inform
the citizens of these problems, and to provide
a guide for developing an effective long-range
program. The survey method utilized measured
the percentage of premises having a particular
environmental sanitation problem within
specified areas of the community. Results
showed that 66 percent or 2,413 of the 3,680
premises, where refuse storage was visible,
were dificient in storage. Types of improper
containers noted were cardboard and wooden
boxes, uncovered cans and barrles, and
damaged and rested containers. It is
recommended that refuse be stored in duable,
flytight, watertight, and rodent proof
containers, cind maintained in a clean condition
and in good repair at all times. Refuse
collection in the consists of garbage
collection by the City and trash collection
by private collectors. Unsatisfactory
conditions are associated with both of these
services. A combined collection system where
mixed refuse is collected together is most
economical. Open burning of refuse continues
to be practiced despite an ordinance that
prohibits it. One percent of the premises
surveyed contained some type of breeding
source for mosquitoes; 8 percent contained
some type of rodent harborage. Recommendations
for eradicating both these problems are given.
65-0075
Cleaning up the world's fair. Refuse
Removal Journal, 8(7):28-29, July 1965.
Four thousand employees of Allied Maintenance
Corp. combine to work continuously day and
night to clean up the refuse generated at
New York's World's Fair. Allied uses a fleet
of Cushman Trucksters and hundreds of
containers for this project.
65-0076
Cleansing conference discussion. Surveyor
and Municipal Engineer, 125(3809):19 , June 5,
1965.
Comments are given on several diverse subjects
covered in papers given at the Institute of
Public Cleansing Conference. R. E. Bevan of
Manchester opposed any system that separated
the responsibility for refuse collection and
disposal. A number of comments were made on
the need for research and it was generally
agreed that this should be done or financed
by the government, and the Institute of
Public Cleansing should initiate steps to
have a research institute for public cleansing
established by the national government. F.
McCarthy of Westminster said that because of
the increasing problems of transport and
controlled tipping, consideration was now
being given to a resumption of incineration.
The price of plastic bins would never be
reasonable for the desired article as long as
each authority wanted its own color and
design. No fully satisfactory plastic bin is
now on the market. The use of plastic
casings for domestic refuse will seriously
limit reclamation. S, Cayton claimed that
plastic bins are so satisfactory that his
authority is not buying any more steel bins.
It was found that refuse in plastic sacks
remained unchanged after months on the tip.
It was held by Mr. Perry that when incineration
returned, as he was certain that it would,
there would be no attempt at salvage and the
refuse would be burned as received. While
there was a suggestion to trust in the traditional
materials, it was indicated that they tended
to increase in cost while plastics became
cheaper and more versatile.
65-0077
Cleansing in Johannesburg.
55(10) :567, Oct. 1965.
Public Cleansing,
The refuse collection, disposal, and street
cleaning services in Johannesburg, South
Africa are described. About 1 ,400 tons of
refuse are deposited daily in 6 sites.
Pilot plant composting is underway. City-owned
refuse bins are being installed. Street
sweeping is done manually.
65-0078
Conference exhibition preview. Public
Cleansing, 55(5)-.238-255 , May 1965.
In June 1965 a conference was held in
Scarborough, England, which included
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0074-0083
exhibitions and demonstrations of British-made
solid-waste management machines. A guide is
presented to the exhibitions, including brief
descriptions of the following equipment: refuse
collection vehicles, street cleaners, storm
sewer and cesspool cleaners, snow clearing
machines, protective clothing, and earth
moving machines.
65-0079
Contractor matches community growth. Refuse
Removal Journal, 8(4):36-37, 50, Apr. 1965.
Among Anaheim Disposal Co.'s industrial and
commercial accounts is Disneyland. The
company grew with the city until today its
16 trucks haul 125 tons of commercial refuse
per day and 75 tons industrial, not including
the Disneyland account in the summer, which
accounts for an additional 50 tons.
65-0080
Crowther, G. Bulky refuse. Public Cleansing,
55(10):599-601, Oct. 1965.
Bulky refuse and logical guideposts for its
control are defined. Cardboard cartons, in
excess, may prompt a separate wastepaper
collection, or may indicate that the regular
dustbin is too small; furniture may be
collected by an open truck once a week from
scheduled areas. Brick and rubble refuse may
be eliminated by educating the public to make
sure that the repair or construction contractor
disposes of his own refuse, though small
amounts of brick or rubble may be accepted at
special collection points. Garden refuse may
be collected on a similar basis to furniture,
with care being taken not to overexpand
disposal services.
65-0081
Editorial reflections--modern history.
Public Cleansing, 55(3):126-128, Mar. 1965.
This editorial scans the modern history of
refuse collection and disposal. It highlights
the organizational change towards regional
refuse disposal in the formation of the
Greater London Council. This regional
approach to disposal allows economic planning,
pooling of resources, and added hygiene and
amenity throughout a large area.
65-0082
Edmunds, J. E., C. K. Wiehle, and K. Kaplan.
Structural debris caused bv nuclear blast.
Burlingame, Calif., TJRS Corporation, Oct.
1964. 63 p.
Postattack recovery and reclamation operations
are concerned, in part, with the production
of debris by total or partial callapse of
buildings and structures. A number of sources
of information were considered in the study:
the atomic bomb attacks on Hiroshima and
Nagasaki; the controlled nuclear weapons
test in Nevada and the Pacific; analyses of
these tests and theoretical studies that lead
to methods for estimating building damage;
the large accidental explosions at South
Amboy and Texas City; and reports on natural
disasters. The objective of the data reduction
portion of the program was to determine the
quantities of debris produced by blast for
as many different structures as possible. From
the data, graphs were prepared relating total
debris production to peak incident overpressure
for 20 kiloton and 20 megaton weapons.
Individual graphs are presented for each of
the six building categories, and the information
is summarized on two combination graphs for
each of the weapon yields, on each of which
debris production curves for all building
categories are plotted. Recommendations for
continued research in this area is given.
(Clearinghouse for Federal Scientific and
Technical Information AD 450 115)
65-0083
Ehlers, V. M., and E. W. Steel. Refuse
sanitation. In Municipal and rural sanitation.
McGraw-Hill Series in Sanitary Science and
Water Resources Engineering. 6th ed. New
York, McGraw-Hill Book Company, 1965. p.151-182.
Collection costs, and quantities of various
wastes that may be expected are discussed and
the terms: refuse, garbage, rubbish, ashes,
dead animals, street sweepings, and industrial
wastes are defined. The efficiency of the
entire collection and disposal system is
partially dependent upon the degree of
individual cooperation accorded the storage
phase. Refuse collection involves municipally
administered programs or contractual operations;
selection and training of collection personnel;
provision of frequent collection services;
selection and maintenance of collection
equipment; and record keeping. Advantages,
disadvantages, and operational techniques of
the following refuse disposal methods are
reviewed: dumping, hog feeding, incineration,
sanitary landfill, composting, discharge to
sewers combined with grinding, and salvage.
For small organized communities, it is
recommended that refuse be collected by the
local government and that disposal be by
sanitary landfill.
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Collection and Disposal -General
65-0084
Everything goes down the drain. Engineering
News Record, 175(21) :107-108, Nov. 18, 1965.
The Matthew Hall Garchey system is described.
Its basic components are a waste-collector
tube that fits into a 5^-diameter drain in
the sink and a Garchey bowl hidden under the
sink that surrounds the waste tube and traps
the waste water drained from the sink. When
the waste tube is full, it is lifted up from
its seating; a flap in the bottom of the tube
opens, and the waste water collected in the
bowl washes the rubbish through vertical
pipework common to several apartments to a
central underground collection chamber. The
system will dispose of such items as potato
peelings, ketchup bottles, soup cans, coffee
grounds, burnt-out light bulbs, etc. Oversized
objects will require secondary garbage
collection. Blockage in the system can be
easily dislodged by poking a rod through the
unit. No electrical parts are needed in this
system. At weekly intervals or longer, a
collection tank truck pumps the garbage from
the chamber. A mechanical ram inside the
truck's tank compacts the contents into
semi-solids and squeezes out most of the
water. A truck drain deposits the excess
water into the sewer. Installation costs of
the system vary from $90 per dwelling to as
high as $340. It has been found economical
and practical in a 2,630 dwelling development
in London.
65-0086
Ferber, M. Waste and garbage removal. Wasser
und Abwasser, 106(48):1333, Dec. 3, 1965.
A handbook on the collection, removal and
utilization of waste and garbage from
households, municipalities, and industries
has been published, as suggested by the
Ministry of Health of the German Government.
The book, written by Walther Kumpf, Kurt Maas
and Hans Straub, published by Erich Schmidt
Verlag, deals with the history of city
cleaning, waste removal as a concern of
the Health Department, iaws and regulations,
statistics, and methods to determine the
composition of waste. The collection,
transportation and elimination of sludges and
oil wastes, costs involved in sanitary
landfills and composting, methods of composting,
and utilization of compost in agriculture,
are discussed. Various types of incinerators
are described and the possibilities of slag
utilization are outlined. (Text-German)
65-0087
Films. Public Cleansing, 55(11):646-649,
Nov. 1965.
Films available on loan from the British
Institute of Cleansing are listed. Eighteen
motion picture films and 10 sets of slides
are available free for training and
illustration purposes related to public
cleansing and refuse disposal.
65-0085
Fast-growing city keeps hauler on the go.
Refuse Removal Journal, 8(8):34, 68, Aug. 1965.
The operations of the Great Western Reclamation
Company, a private contractor which
successfully meets Santa Ana's mounting refuse
handling needs are described. It serves the
entire municipality, including commercial,
industrial and all residential accounts. Only
front-end loaders are employed for both
container and residential service.
Containerized service is operated on a 24-hr-a-day
basis, while the downtown commercial zone
must be handled on a night collection
schedule. The firm uses two landfills and
one transfer station for disposal. Through
sanitary landfills much useful ground has
been reclaimed. Maintenance and repair is
handled by a permanent three-man crew that
has prevented any significant interruption in
service in 2 years.
65-0088
First and last place big league ball teams
use same contractors. Refuse Removal Journal,
8(1):8-9, Jan. 1965.
Derrico Bros, of the Bronx service Shea
Stadium, home of the New York Mets and the
Jets, and Yankee Stadium, home of the Yankees
and the football Giants. One and one-half
yard containers store the refuse until pickup.
65-0089
Fleetwood, J. E. Current influences on refuse
collection. Surveyor and Municipal Engineer,
125(3809) :47-49, June 5, 1965.
Although the producer of refuse is only
concerned with the storage on his premises and
its timely removal, there must be a
well-organized use of labor and machinery to
remove the refuse from the premises to the
disposal area in the most efficient manner.
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0084-0092
The three main factors which must be
considered are: What is the material
produced? How and where shall it be stored
on the premises? and How shall it be removed?
The answer to he question concerning what is
produced is 'anything', although this
consideration is limited to domestic refuse
and refuse of a like character. The quantity of
refuse varies with the affluence of the area.
A higher standard of living has resulted in
more cans from pet foods, more children's toys,
more perambulators, refrigerators, washing
machines, bedsteads, and mattresses. The
increased consumption of wines and spirits
has increased the yield of bottles and glass.
With the decrease in solid fuel devices in
the household, there is an increase in the
volume of refuse including an increasing
number of offensive articles. The paper sack
is probably the most hygienic method of
storage and removal of refuse. Once the
method of storage is decided upon, such as
paper sacks, dustbins, or containers, the
location of these devices must be convenient
to the householder and the refuse collection
vehicle. The problem of removal is a matter
of men and vehicles. While the vehicles can
be obtained in the desired design, there is
a problem with the men in training them to
the requirements of the job. It is important
to impress the men with the importance of
their work. Changes in refuse must be met
by changes in disposal.
65-0090
Garchey system tests. Public Cleansing,
55(2):115-117, Feb. 1965.
The new Garchey method of refuse collection
by tanker truck is outlined. Several
multi-story housing developments in London,
Sheffield, and Leeds in England are equipped
with this system. All possible refuse is
washed down the sink to a common collecting
tank. The resulting slurry is periodically
pumped into the tanker truck, excess water
flowing from the truck to the sewer. Tests
show about 90 percent by weight of all
household refuse can be collected in this
manner, the remainder being dry and requiring
infrequent collection. The refuse from 300
dwellings can be collected in 3 hr in one
load. The system is very sanitary as the
refuse is enclosed from sink to disposal site.
Diagrams of the Garchey system are included.
65-0091
Gaskell, J. Public cleansing. Public Health
Inspector, 73(8):331-337, May 1965.
The weight of refuse collected continues to
rise while the yield per house is declining.
Refuse is increasing in volume and bulk while
decreasing in density. There are many
methods of collection and disposal. Disposal
of refuse at the source by sink grinders and
incinerators located in the apartment complex
has grown in popularity, but cannot be
applied to every dwelling. Systems of
collection, which use specially-adapted
trucks or paper sacks instead of bins, have
recently been looked upon with considerable
interest. Controlled tipping is the most
widely used method of disposal and, when
operated in the proper manner, is quite
desirable. Direct incineration has declined
in popularity because of ash accumulation and
odor problems, but may evolve again as the
amount of combustible matter increases.
Separation incineration is more desirable
because only about 25 percent of the original
material remains to be disposed of after
treatment. Pulverization is a pretreatment
process which is costly and not sufficiently
hygienic, but is a good addition to a controlled
tipping program. Composting is not feasible
in industrial areas, but aids the build up
of rural soil. Still, it cannot be looked
upon as the complete answer to disposal.
Labor in this field presents a problem that
can be solved by improving existing conditions
and the public image. New disposal plants
should be built to modern standards and be
fully mechanized. A pooling of local
authority both financial and otherwise is
necessary to build them.
650092
George, J. C. Recreational area sanitation;
refuse handling. In Proceedings; First
Conference, Recreation Sanitation and Safety,
Little Rock, May 25-26, 1965. Dallas, U.S.
Public Health Service, p.71-72.
Proper storage is of upmost importance if
recreational areas are to be free from rats,
flies, and the junkyard appearance. There
must be adequate numbers of well-placed,
watertight, rust-resistant, easily washable
containers. If the conventional 20 to 30
gal cans meet these criteria, they are
acceptable, with certain qualifications, such
as container racks which are mandatory for
the lightweight type of cans. Racks in
recreational areas should be constructed so
that wild animals will not upset the cans.
Fifty-five gal oil drums make excellent storage
containers if tight fitting lids and handles
are provided. For campgrounds approximately
0.18 cu ft per person per day of refuse can
be expected. Based on this, a 30 gal
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Collection and Disposal-General
container can accommodate 30 campers for one
day. Twice a week or as much as daily
collection is necessary for recreational areas
depending on the usage. Acceptable collection
vehicles are trucks with watertight, covered
beds, closed bed or flat bed if container
exchange is used. Packer trucks are ideal.
Some modification of a sanitarv landfill is
necessary in recreational areas because of
haul distances. A trench, or several trenches,
strategically located, can serve several of
the recreational areas.
65-0093
Growing pains. Refuse Removal Journal, 8(8):30,
Aug. 1965.
To meet the rapid expansion of metropolitan
areas, refuse collection and disposal should
be administered on a city-wide basis by
contract with both public and private refuse
contractors.
65-0034
Hudson, B. J. Refuse disposal. U'estern City,
41(7) :40, July 1965.
A report of 164 Oregon cities has been issued
by the Oregon Bureau of Municipal Research
and Service. For refuse collection and
disposal a majority of cities gave an
exclusive license to a private firm or assume
direct municipal responsibility thenselves
either by contract with a private firm or by
use of city equipment and personnel. Most
cities charge a franchise or license fee,
with fees ranging from $.75 to S3.50 with the
average between $1.25 and $1.75. In Oregon
the trend is toward the packer trucks for
efficiency and savings. Sanitary landfills
are also gaining public acceptance.
65-0095
Hume, N. B. A million stops daily in Los
Angles. Refuse Removal Journal 8(8):38, 50,
52, Aug. 1965.
Los Angeles employes 1,350 workers to collect
and dispose of 1.1 million tons of refuse
from residential areas and a small ouantity
of commercial and industrial refuse. The
city uses 433 packer trucks for its residential
pickups. Food wastes [rom hotels and
restaurants aresold to hog raisers. Dead
animals go to processing plants, but the bulk
of the refuse is buried in city or county-owned
landfills. Refuse is not incinerated because
of the city's severe smog problem.
65-0096
Kauoert, W. Meeting of the association of
municipal waste collection and city cleaning
departments. Satedtehygiene, 16(2):45-47,
Feb. 1965.
A meetina of the association of municipal waste
collection and city cleaning departments was
held in Munich between October 20 and 23, 1964.
A number of waste disposal problems were
discussed. Since 1950 an increase of waste
by 120 percent was recorded and of sludge by
180 percent. The basic requirements for
controlled dumping were reviewed, and the costs
were discussed. It was found that generally
the costs average 0.5 to 1 D'-' per cu m.
Street cleaning problems were also briefly
considered. (Text-German)
65-0097
Knowler, W. E. Everyone in Sanford, Florida,
likes the sanitation men. Refuse Removal
Journal, 8(5):20, 42, May 1965.
Sanford, Florida, augments its public image
with the use of modern collection packers
and trained men in city uniforms. The city
also provides written stipulation on the
storage cf refuse. Other keys to a good
refuse system are: use of large 'tote
barrels' to reduce trips to the packer trucks,
high employee morale, and the recovery of low
waste land bv means of a sanitary landfill.
65-0098
Kumpf, W. K. Maas, and H. Straub. Refuse and
waste disposal. Berlin, Druckhaus Lichterfeld
GmbH, 1964.
A handbook for the collection, removal, and
utilization of household, municipal and
commercial waste is presented. Collection and
disposal of waste has within a few years
become a very important and urgent problem.
A brief history of city sanitation is presented.
The historical relation between municipal
sanitation and general health is reviewed.
Legal and administrative regulations applying
to waste disposal are included. The relation
between regional planning and disposal of
solid waste is considered from the angle of
planning legislation. Types of liquid and
solid waste are discussed. Technical terms
used in solid waste management and their
definitions are presented. The amount and
composition of solid waste and special
vehicles for refuse collection and discussed.
The collection and removal of liquid sludge
and city refuse and the disinfection and
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0093-0103
devitalization of solid and liquid waste are
considered. This work is intended primarily
for communities and enterprises directly
concerned with this field, but also for
planning experts and for authorities which
askess and approve proposed measures.
65-0099
Kumpf, W., and H. Straub. Introduction and
survey. In Refuse and waste disposal. Berlin,
Druckhaus Lichterfeld GmbH, 1964.
Representatives and delegates of numerous
communities travel as far as the United States
to gather information and to obtain suitable
solutions in their own sphere of activity.
But conditions in one country or even in one
community cannot be mechanically applies to
another. The danger of incorrect technical
decisions and faulty financial investments is
therefore great. As early as before World
War II the Deutsche Gemeindetag and the then
existing Prussian Institute for Water, Soil,
and Air Hygiene in Berlin-Dahlem dealt with
the removal of waste. After the war other
associations and scientific institutions
also studied this topic. Recently political
circles have also begun to take part. In
several State Diets, there have been discussions
on the difficulties and possibilities of
improvement. All the positive and negative
aspects of the different methods of disposal
have to be carefully weighed and compared.
Construction and operating costs may also be
decisive. The First Report of the Federal
Government on Jan. 31, 1963 to the Federal
Parliament is presented. The Second Report
of the Federal Government on the Problem of
Waste Removal was submitted to the Federal
Parliament on Jan. 28, 1966. This is also
presented along with subsequent measures and
their results significant to developments in
waste economy.
65-0100
Meeting of the Bremen, Hamburg, Niedersachsen,
and Schleswig-Holstein work groups of the
Department for Municipal Waste Collection
and City Cleaning, Staedtehygiene,
16(12) :277, Dec. 1965.
On November 18 and 19, 1965, the Bremen,
Hamburg, Niedersachsen and Schleswig-Holstein
work groups of the Department for Municipal
Waste Collection and City Cleaning held a
meeting. Several papers were presented.
The most interesting one dealt with the
possibility of dumping the waste into the
ocean. No details of the paper are discussed.
(Text-German)
65-0101
New Canadian trash baling plan may save city
$100,000 yearly. Refuse Removal Journal,
8(4):39, Apr. 1965.
Packer trucks in Hamilton, Ontario, haul
refuse to a compressor which meshes it into
a bale, one twentieth its original volume.
This system cuts transportation costs and
greatly extends the life of the city's
landfill.
65-0101
Night people labor behind the scenes in New
York City. Refuse Removal Journal, 8(6):35,
June 1965.
Night people are a key factor in the smooth
operation of the New York City Department of
Sanitation. Besides around-the-clock teams
who operate collection trucks, there are
24-hr watches at the incinerator and transfer
operations and aboard the Department's "Navy'.
About 15 men are on the night shift at the
incinerator operation, less than half the
number required to work the day watch. The
night job requires a stationary engineer,
incinerator foreman, stationary fireman,
crane operator, and checkers at the transfer
station. The Department of Sanitation
tugboats which tow refuse-laden scows to
the huge Staten Island sanitary landfill, also
operate through the night. From the
incinerator, with four refuse-laden barges,
to the Staten Island landfill, the round
trip, with another stop in Brooklyn, is 9 hr.
65-0103
Noppen, A. M. Refuse collection and disposal
in the Netherlands. In American Public Works
Association Yearbook, 1965. Chicago,
American Public Works Association, p.232-245.
In an effort to eliminate the refuse
accumulating on the street the Corporation of
Amsterdam in 1930 started issuing to each
household a standard-sized refuse bin (33
liter capacity) which could be emptied
practically dust-free into specially built
collection trucks. About 3 and 1/3 million
of these refuse bins have an average life of
12 years, and their introduction was followed
by a mechanization of the whole collection
system involving collection trucks with
detachable containers of 6 cu m. These
containers were exchanged for empty ones by
3 ton cranes at 10 points throughout the city
along canals where they were loaded on barges,
and then towed to the incineration plant.
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Collection and Disposal-General
More paper was used after World War I],
resulting in the doubling of the volume of
refuse collected per person per year in the
last 15 years. Because of this change in
composition of the refuse, it was necessary
to compress it, and various packing trucks
were introduced. The recent construction of
apartment houses has created the problem of
transporting the refuse bins in these
multi-story buildings. Chutes have provided
the most acceptable answer* As a result of
the demand for compost which had to meet
higher standards, a Refuse Removal and
Compost Manufacturing Company, the VAM, was
founded in 1930. The composting process is
described. The demand for high-grade compost
has resulted in the employment of the Dano
or the Rasp-system by some towns.
65-0 W
Parkhurst, J. D. Refuse handling techniques
and developments. In American Public Works
Association Yearbook, 1965. Chicago, American
Public Works Association, p.254-257.
Refuse collection and disposal practices in
Los Angeles County are traced. A report,
'Planned Refuse Disposal' , submitted by the
Sanitation Districts of Los Angeles County in
1955, indicated a haphazard and unsophisticated
collection of refuse by present standards.
The report concluded that the only logical
method of disposal was sanitary landfilling.
It was recommended that the Sanitary Districts
finance, acquire, and operate the sites,
and five major landfills have been established
which presently dispose of about 11,000 tons
of refuse per working day, about half the
refuse produced in the County. The basic
conclusions of the report have proved correct.
Each day's refuse is compacted into a
single mass and then covered with a layer of
earth at the close of the day's operation.
No mechanical compaction is applied to the
refuse other than that of the crawler tractors.
Self-propelled, rubber-tired scrapers are
currently being used to excavate and haul
cover material. Water wagons are used for
dust control on roadways and at the dumping
area. The per ton operating costs at the
Districts' landfills have remained stable and
even decreased slightly in an 8 year period
during which general construction costs rose
about 30 percent. The 1955 report recommended
transfer stations in some areas and one is in
operation in South Gate, California. Even
though potential landfill sites are still
available, other methods of disposal such
as composting and disposal in the ocean are
under study.
65-0105
Pollock, E. L. England's oldest 'haulier'
serves nation's industrial hub. Refuse Removal
Journal, 8(9):8-9, 42, Sept. 1965.
Thomas Hancock, Ltd., England's oldest refuse
contractor company, collects industrial and
railroad refuse and operates 28 landfill
sites in England's industrial centers of
Manchester, Birmingham, Lancashire, North
Midlands, Stokes, and North Wales. The
Hancock vehicles have a built-in lubrication
system, which has increased the life of truck
equipment by 50 percent. Hancock is also a
pioneer in containerization.
65-0106
Refuse. In Environmental health report of
Savannah and Chatham, Georgia. Savannah, Ga.,
Commissioners of Chatham County, June 1965.
Section 111.
The two municipal landfills now in operation
(Savannah and Savannah Beach) as well as the
method of collection in these municipalities
and the unincorporated areas are brielfy
examined. Currently, the City of Savannah
is operating a 35-acre landfill and permits
refuse disposal for all of Chatham County with
the exception of Savannah Beach. Savannah
and Chatham County do not have adequate
ordinances to institute and maintain control
of solid waste storage, collection, and
disposal. Residential (52,366 units) refuse
is picked up twice weekly and commercial pickup
is two to six times per week according to
need. Several unsupervised disposal areas
exist in the county. The sanitary landfill
in the City of Savannah is operated in
accordance with the recommended practices of
the U.S. Public Health Service. By 1985,
Chatham County will have a projected
population of 286,000. At the current rate
of land usage, approximately 28.6 acres per
year will be required. A list of recommendations
for future action is furnished. The study is
co-sponsored by the Savannah Area Chamber of
Commerce, Chatham County Health Department.
in cooperation with Georgia Department of
Public Health, University of Georgia, Georgia
Department of Industry and Trade, and the
U.S. Public Health Service.
65-0107
Refuse, In Environmental health
survey--Gainesville, Florida. Gainesville
Florida State Board of Health, Apr. 1965.
p.16-18.
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0104-0111
Gainesville, population 60,000, generates
about 150 tons of garbage household, commercial,
and industrial wastes per day. By 1985,
when the population is expected to reach
96,000, the solid waste is expected to reach
240 tons per day. Four areas are considered
in the present methods of solid waste
collection and disposal: The City of
Gainesville, the suburban area, The University
of Florida, and Sunland Training Center. In
the City of Gainesville, a refuse collection
service is operated by the Public Works
Department and households are charged $1.50
per month. A private collector firm provides
services for the suburban area at a cost of
$2.00 per month. The University of Florida
uses incineration for its refuse. Air
pollution is a source of annoyance on the
campus. The Sunland Training Center disposes
of its refuse to a pig farm, and the remainder
is incinerated and landfilled. A list of
recommendations is furnished for Gainesville.
The survey is co-sponsored by The University
of Florida in cooperation with Alachua County
Health Department and assistance from the U.S.
Public Health Service.
65-0108
Refuse collection and disposal. In
Environmental health survey, Carbondale, 111.
U.S. Public Health Service, 1965. p.31-35.
A seven-member advisory council on the
problems of refuse collection made a report
to the Carbondale City Council, and excerpts
of that report are given. The need for
regulation and implementation of proper refuse
storage, collection, and disposal is not only
for considerations such as eliminating
unsightliness and odors in the city, but the
presence of improper storage, collection, and
disposal methods of garbage and rubbish will
give rise to large populations of flies, rodents,
and mosquitoes. These vectors transmit many
diseases to cause individual health hazards.
The projected population for Carbondale is
81,000 for 1985. The estimated amount
of waste for the population would be 204 tons.
Currently, there are no required specifications
that need be met for containers for the
storage of refuse. Solid waste is being
collected by the city plus private scavengers,
and the refuse is disposed of in the city
operated sanitary landfill. The site is not
ideal as a portion of the area is occasionally
flooded with back water, and water often
stands in the trench during rainy periods.
Aside from mosquito control, there have been
outbreaks of diseases related to vectors;
more stringent controls should be exercised.
A list of recommendations and illustrations
are furnished.
65-0)09
Refuse collection and disposal in Kenosha.
Public Works, 96(7):135, July 1965.
During 1964, Kenosha, Wisconsin, collected
12,296 tons of combustibles. The cost for
collection and incineration was $21.25 per
ton; the cost for incineration being about
$3.85 per ton. In all, 15,019 tons were
incinerated; residue from the incinerator
amounted to 3,185 tons. The city also
collected 13,098 tons of non-combustibles which
cost $16.67 per ton for collection and dump
maintenance, of which $1.57 was for dump
maintenance. Including non-combustibles from
other sources, total material received at the
dump was 35,219 tons.
65-0110
Refuse collection & disposal practices.
Austin, Texas Municipal League, Oct. 1965.
187 p.
This publication gives information and data
on refuse collection and disposal practices
in Texas communities. William A. Olsen
explains legal opinions supported by selected
law cases. General data on collection is given
for Texas Cities (A) ; Salaries and wages of
superintendents and collectors are shown by
cities (B); and Work-week hours are shown in
Table C. Frequency of collection and type of
equipment are given in Table D. Table E shows
customer requirements and disposal facilities.
Residential collection fees are listed in
charts F and H; and commercial collection
fees, in G and I. Table K gives miscellaneous
fees. Section L describes cities not listed
in the statistical tables. M includes sample
ordinances and regulations while section N
shows sample contracts and regulations.
Sample forms and notices are given in
exhibit 0.
65-0111
Refuse collection problems. Surveyor and
Municipal Engineer, 125(3812) : 36 , June 26,
1965.
This article covers the discussion on a paper
by J. E. Fleetwood titled, 'Current Influences
on Refuse Collection'. J. R. Willson of
Bournemouth said that, because his community
had a high percentage of retired and wealthy
people, all refuse contained in the bins
was removed and the residents could have as
many bins as they wanted. Apparently the
3 \-c\i ft bin is too small for present day
requirements. The paper sack and the plastic
bin have made collection much easier. In
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Collection and Disposal-General
Northampton, one driver and three loaders
making two weekly curbside collections, removed
900 to 1,000 bins a day of \\ to 2-cu ft size,
but one man added made little difference in
the collections. It was stated that only
the worst type of help would be available,
irrespective of the pay rates, because of the
working conditions. It was also indicated
that as long as men with families could earn
more on relief than they could by emptying
bins, there would be a serious shortage of
labor for this sort of work. Abandoned cars
should be reiroved and stored for the period
required by law and then disposed of
satisfactorily. Architects should be told
of the problem of the cleansins services so
that provision could be made in the original
plants for location of bins. No sink
grinders should be permitted without approval
of the sewage disposal authority. Industrial
wastes should be handled by private contractors
as long as their serviceis satisfactory.
The only feasible method of disposing
of fireworks is in a trade waste incinerator.
65-0112
Rockey, J. W. Disposal of wastes. In
Consumers all--the yearbook of agriculture
1965. Washington, U.S. Government Printing
Office, 1965. p.38-42.
Consult local health authorities before
building houses or sewage disposal facilities.
Discarded paper products and clothing should
be kept from sevage disposal systems. Dispose
of fecal excreta without contaminating water.
A septic tank does not purify, deodorize or
destroy solids; it conditions through partial
settling and decomposition for soil absorption.
As a charge of sewage enters the tank from
the house, it displaces an equal volume of
conditioned effluent which is discharged to
the absorptior area. The absorption area
should be at 3 lower elevation and at least
100 ft from any water source and 10 ft Erom
dwelling or property line. If the house has
a garbage disposer, allow 50 percent extra
tank capacity. A tank should be inspected
annually and cleaned by pumping wher the
combined depth of sludge at the bottom and
scum at the top reach 1/3 the liquid depth of
the tank. A privy should be at least 50 ft
from the house. A 50-cu ft capacity pit
should serve a family of five for 5 to 10
years. Capacity data is given. Commercial
deodorants reduce odors. Garbage should be
held in covered, watertight, rustproof,
containers, cleaned at least weekly. Material
may be compacted or burned and then covered
in trenches 3 or 4 ft wide, 4 or 5 ft deep,
and 7 or 8 ft Long. Keep the pile moist to
facilitate rotting if making compost.
65-0113
Roeder, W. F. Odors curtailed at transfer
point close to capitol hill. Refuse Removal
Journal, 8(7):14, 22, 26-27, July 1965.
Washington, D.C., built a transfer station in
the heart of the city, designed to eliminate
odor and dust. The city tries to reduce its
refuse by every possible means without
resorting to low ground. Hence, garbage is
hauled off to feed over 30,000 pigs in the
area; leaves are composted; incinerator ash
is used by private and public agencies; and
the remaining refuse is transferred to a
landfill.
65-0114
Magnitude of the problem. In Restoring the
quality of our environment. Report of the
Environmental Pollution Panel, President's
Science Advisory Committee. Washington, U.S.
Government Printing Office, Nov. 1965. p.140-142.
Comprehensive statistics on the magnitude of
all solid waste generated in the United States
are not available, but even a cursory view
gives the impression that mankind is rapidly
engulfing itself in its own debris. Data is
presented to convey a picture of the quantities
of waste and the dollar figures involved in
treatment, disposal, and salvage. It is
intended to provide a frame of reference
rather than an approximate compilation of the
gross quantity. A frequently quoted estimate
of the unit output of municipal solid waste
is 1,600 Ib per capita per year or 4.5 Ib
per capita per day. For our present
population this means 250 billion Ib of
municipal solid waste per year. The collection
and disposal costs are estimated to be 1.5 to
2.5 billion dollars. By 1980, the per capita
output is estimated to be 5.5 Ib per day.
Other figures are included which present
quantities of waste generated by paper,
containers, mining operations, demolition
sites, etc.
65-0115
Stirrup, F. L. Other disposal systems and
the disposal of trade waste. In Public
Cleansing; refuse disposal. Oxford, The
Institute of Public Cleansing, 1965.
p.137-144.
The Garchey system is a water-borne system
where refuse must flow freely. There is a
unit in the house where refuse is discharged
through the top opening without grinding.
Overflow piles allow surplus water to discharge
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0112-0119
directly to soil drains. To avoid excessive-
use of water, use waste water. The Matthew
Hall-Garchey system eliminates the incinerator.
Refuse remains within the collection chamber
instead of passing to the disposal unit.
Collection vehicles can reduce bulk by
disintegration and pakcing as opposed to the
normal compression vehicles how used. A
Compressing Refuse Collector, which was
available in Great Britain, provides the
principle upon which such a system could be
based. Refuse is loaded through the rear,
tumbling against the blades, forced forward,
and packed by the weight of the incoming
material. Domestic incinerators are expensive
and not always hygienic. Disposal of trade
and industrial wastes present a question. Are
waste from manufacturers the responsibility
of the producer, or should municipalities
undertake disposal and charge for services
levied? The accent is upon recovery of
waste material and its utilization within the
industry or as raw material for some other
product.
65-0116
Stirrup, F. L. Public cleansing; refuse
disposal. Oxford, The Institute of Public
Cleansing, 1965. 44 p.
This book has ten chapters: (1) Introduction;
(2) Refuse composition which includes: seasonal
analysis, classes of property, conversion
formula, procedure, records, material
characteristics, comparative analysis and its
use; (3) Assessing disposal methods which
concerns: tabular assessment, questions to
be answered, legal position, amenity,
temperature and climate, material utilization,
and beneficial usage; (4) Controlled tipping
which discusses: precautions, processes,
bacterial action, temperatures, gases, metal
breakdown, site selection and value, Liverpool's
land recovery, area required, site operation,
preparation, soil stripping, tip loads, culverts,
drains, methods, layers, litter prevention,
covering material, waterlogged areas, equipment,
cost, vectors, and future use; (5) Transfer
loading stations which covers: simple transfer
stations, purpose types, compaction, bulk
reduction M.P.L. system, and rail and water
transport; (6) Pulverization and grinding
which concerns: the pulverizer wear, nature
of refuse, types of pulverizers and grinders,
and effects of ground material in tips; (7)
Composting which includes: history, use of
sludge, manure formation, systems, and
processes; (8) Incineration which discusses:
refuse analysis, sites, dust extraction,
furnaces, and grates; (9) Salvage and
utilization which covers: waste paper, baler,
boxes, metals, textiles, glass, by-products;
and (10) Other disposal systems and the
disposal of trade wastes.
65-0117
Study probes a single waste system. American
City, 80(6):168, June 1965.
Aerojet-General is assigned to an extensive
study of waste management control and the
possibility of considering sewage, refuse,
and air pollution as one system under a
$100,000 contract with the state of California.
65-0118
Tauber, F. 'Pro Aqua' Exhibition in Basel,
Switzerland. Staedtehygiene , 16(9) :208-209 ,
Sept. 1965.
Approximately 200 companies from 11 states
participated in the 'Pro Aqua' exhibition in
Basel, Switzerland. The Passavant sludge/ash
process in which the sludge is dehydrated in
a filter press and subsequently incinerated,
was demonstrated. Moreover, various types of
waste collecting trucks and hammer mills for
crushing the waste were on display. The
incinerator, displayed by the Machine
Manufacturing Company Esslingen, West Germany,
aims at discharging a completely sterilized
slag. The Koopers Wistra Furnace Manufacturing
Company offered a plant for incinerating acid
resins and oily resins. The companies
Buehler and Dane displayed composting plants
and magnetic drums. (Text-German)
65-0119
Walton, G. Institutional sanitation. 2d ed.
Washington, U.S. Bureau of Prisons, 1965. 322 p.
This revised edition is designed for institutions
such as prisons to aid in establishing and
maintaining sanitation programs. The
sanitation problems of the Federal Bureau of
Prisons are similar to any other community's
problems of water supply, waste disposal,
food sanitation, rodent and insect control,
and housing. Institutional sanitation is
effected by: personnel of the U.S. Public
Health Service, the chief medical officer of
the institution, or the sanitary supervisor,
who is a service officer with limited training
in sanitation. The purpose of this manual is
to provide guidance for the sanitary supervisor.
Standards of sanitation have been selected,
the scope and nature of the work to be
performed by the sanitary supervisor is
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Collection and Transportation of Refuse
indicated, and useful information with
respect to the performance of duties is
provided. The contents include: The Sanitary
Supervisor & His Work, Introduction to
Bacteriology, Communicable Diseases, Water
Supply Sanitation, Plumbing, Bathing & Pool
Sanitation, Sewerage & Sewage Treatment,
Garbage & Other Refuse, Food Service Sanitation,
Canning Sanitation, Milk Sanitation, Ice
Sanitation, Meat & Slaughterhouse Sanitation,
Public Health in Housing, Housekeeping,
Control of Insects & Other Arthropods, Rodent
Control, Disinfection & isinfestation of
Bedding & Clothing, Barber Shop Sanitation,
Industrial Hygiene Engineering, Radiation
Protection, and Sanitation Test Equipnent &
Its Use. An index is included.
non-combustibles is not normally approved,
but appears to be satisfactory for the peculiar
situation existing at Kwajalein. Incineration
is not recommended because of the cost. The
present methods of disposal at the Kwajalein
site are regarded as unsatisfactory because
of health, nuisance, and safety hazards that
are created. These hazards are summarized.
Recommendations are made for the extensive
use of sanitary landfill, composting, and
barging to Carlos Island. Costs for these
methods are given.
COLLECTION AND TRANSPORTATION
OF REFUSE
65-0120
What was on show at Scarborough. Public
Cleansing, 55(9):502-514 , Sept. 1965.
The 1965 Scarborough, England, exhibition of
refuse collection and disposal equipment in
Britain including remarks on the machine
demonstrations is reviewed. Packers, street
cleaners, container handlers, gully cleaners,
protective clothing, and landfill equipment
are discussed and illustrated.
65-0121
Wiley, J. S. Report of a special study of
refuse disposal at Kwajalein Island, Kwagalein
Atoll, Northern Marshall, Apr. 20-23, 1964.
San Francisco, U.S. Department of Health,
Education, and Welfare, 1964. 11 -3.
Kwajalein Island has a population of about
3,900. Refuse is collected every two days
from the various civilian and military
installations of Kwajalein. Refuse, except
for the separately collected garbage, is
dumped along the south side of the west end of
the island. At intervals the refuse is burned
as much as possible. After burning, t4e
unburned refuse is bulldozed over the berm
into the ocean. Yearly estimated amounts of
refuse, based on a 6-day collection week, are
emthod of refuse disposal is the most widely
used generally the least expensive approved
method of disposal. Properly operated sanitary
landfills will eliminate all of the health
and nuisance factors associated with open or
burning dumps. An alternate method of
disposal consists of separation and composting
of the combustible refuse with ocean disoosal
of the non-combustible wastes. Barging refuse
and garbage to isolated areas, with burning
of combustibles and ocean disposal of
65-0122
Andrews, L. H. Refuse trains keep trash
collection on schedule. American City,
80(9):18, Sept. 1965.
For the past 8 months, six refuse trains have
collected brush once a week in St. Petersburg,
Florida. Each train consists of either three
LoDal or three Dempster trailers towed by
Ford or Chevrolet !>>- or 3r-ton pick-up trucks.
Two 24-yd consolidation packers, one LoDal
and one Dempster, act as 'Mother Packers'
for the trains. The trains augment the
collection service provided by a fleet of
28 trucks, and service nearly all sections
of the city. Since the low trailer beds
facilitate the loading of brush and grass, the
trains were found more effective for brush
than for garbage collection. Recently,
eight 20-yd Garwood packer units mounted on
International chassis were added to the
sanitation fleet for garbage collection.
65-0123
Ballard, M. A. A golf-cart refuse toter.
American City, 80(6)-.61 , June 1965.
Two North Carolina towns found refuse handling
easier, more efficient and less-accident-causin.g
if tubs used for back-door pick-up were on
wheels. An oversized golf cart designed to
carry a 50-gal toter was developed. The
toters have reduced collection crews from
five to four and have allowed a $9,000 budget
cut.
65-0124
Baumann, H. Collection and removal of solid
waste. In Refuse and waste disposal. Berlin,
Druckhaus Lichterfeld GmbH, 1964.
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0120-0130
Special vehicles for refuse collection are
discussed. This includes principles of design
and operation of refuse-collecting vehicles,
open vehicles, vehicles with closed bodies,
vehicles of closed design for dustless refuse
collection, special vehicles, transport vehicles
with large receptacles, vehicles for transporting
bulky refuse and bulky loads, and vehicles
for transporting bulk containers. Vehicles
with closed bodies, devices for compressing
the refuse, and universal receivers at the
vehicle rear are also discussed.
65-0125
British Anzani developing detachable skips.
Waste Trade World, 107(26):7, 9, Dec. 25, 1965.
The large-scale development of detachable
skips for scrap handling and transportation
is described. Although skips have been used
in scrapyards in conjunction with cranes,
their use as detachable truck bodies on a
standard chassis fitted with a hydraulic
loading/unloading mechanism is comparatively
new. Advantages include ease and speed of
handling, one-man operation throughout, dual
purpose transportation, tidiness, and
uniformity in day-to-day operation. The skip
can be loaded or unloaded in 30 seconds in a
push-button operation. The only manual effort
is the releasing or attaching of the hooks
which secure the container during transit.
The adapted vehicle can be used either as a
detachable skip transporter or as a dumper;
the bottom is completely sealed, making it
useful for handling such materials as
oil-contaminated swarf. One standard truck
chassis, fitted with the hydraulic attachment,
can handle scores of skips and maintain an
efficient and economical site-clearance
service. Two models are available: the
standard skip with a capacity of about 6 tons
and the extended skip which is 2 ft higher
with a capacity of 8 tons.
65-0126
Central lubricant system installed in 100
Detroit packer units. Refuse Removal Journal,
8(12):14, 16, Dec. 1965.
Types of central lubricating devices for
refuse vehicle fleets which provide timed,
automatic greasing of vital bearings and
points from a self-contained unit are
described. Average manual lubrication
frequency in the refuse industry is 32 times
a year. Advantages of central, automatic
systems are better equipment maintenance and
less off-time for service.
65-0127
Collection method issue raised again. Refuse
Removal Journal, 8(6):32, June 1965.
The question of rear-door collection versus
curbside pickup, a concern of residents for
over 30 years, was raised again in Millburn,
New Jersey. The present operation requires
residents to carry their refuse cans at night
and return them in the morning when emptied.
Often the cans stay in front of homes all day,
an unsightly practice. A rear-door collection
system would cost the community up to $150,000
more, which might mean a 7-point tax rise to
the community. The rear-door collection had
been tried in the 30's but it was dropped
because of the extra work involved. Various
civic organizations have suggested changes
from time to time such as a study to determine
the cost of rear-door collection. One civic
association supported a compromise solution,
suggesting that residents carry the cans out,
and collectors haul them back to the rear door.
65-0128
College co-ed cleans vehicle and helps dad
on collection route. Refuse Removal Journal,
8(2) :18, 30, Feb. 1965.
Kilbride's Refuse Service of Amherst, Ohio,
uses a unique water tank and pump system
attached to its chassis to clean its customers'
containers. The Company operates one truck.
65-0129
Current influences on refuse collection.
Public Cleansing, 55(8):474-477, Aug. 1965.
Many British homes have two 3k-cu-ft garbage
cans. The refuse volume appears to be
increasing, but the refuse collectors' work
load is lightened with paper sacks and plastic
cans. The work output of 1,000 cans per day
with a 3-man team plus drive was not
commensurately increased with a 4-man team.
Architects need to be more aware of the
necessity for designing economical and
practical refuse disposal for buildings and
homes.
65-0130
Danforth, H. L. How to solve the holiday
collection problem. American City, 80(3):20,
Mar. 1965.
Tucson, Arizona, solved the holiday collection
problem by squeezing its regular collection
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Collection and Transportation of Refuse
into four days instead of five, leaving
Wednesday and Saturday open for trash
collection when a holiday falls on one of the
regular scheduled days. A new train system,
which has shown substantial savings, collects
65 percent of the refuse.
650131
Denver builds transfer station. Refuse
Removal Journal, 8(5):32, May 1965.
Denver, Colorado, is building a trash transfer
station, which will be a roofed, reinforced
concrete building with two ramps. Collection
trucks will dump refuse from the upper ramp
to the transfer trucks on the lower ramp.
65-0132
An editorial. Refuse Removal Journal,
8(1) :14, Jan. 1965.
A few changes in refuse collection over the
past 8 years including the rise of
containerization, the switch from open body
trucks to compacting refuse body trucks, and
the rise of local and regional organizations
are noted. The Journal's influence on the
Sanitation Industry is discussed.
65-0133
An editorial. Refuse Removal Journal,
8(7) :12, July 1965.
A progressive; refuse collection operation
sets aside a portion of its operating costs
for advertisement and business promotion and
entertainment. The schedule of operating
costs published in the 1965 Sanitation
Industry Yearbook provides guidelines for
establishing rates.
650135
Efficient and noiseless waste removal.
Staedtehygiene, 16(5):126 , May 1965.
The municipal street cleaning department in
Duesseldorf, West Germany, introduced a new
lift and tipping mechanism on their waste
removal trucks. The full containers are
picked up noiselessly by the trucks. At the
disposal site or at the incinerator plant the
containers are hydraulically tipped and
emptied. "Fifty or 60 containers--the exact
number depends on the distance between the
disposal site and the location of the
containers--can be picked up by one truck.
An empty container is left instead. The new
method is quite advantageous. It saves
personnel, the load-up and unloading takes
only 3 minutes, and space is saved. The large
container can hold the waste of 40 waste cans.
(Text-German)
65-0136
Employees suspended for stopping work.
Removal Journal, 8(2):27, Feb. 1965.
Refuse
The Civil Service Commission of St. Louis,
Missouri, has set aside a part of the
suspensions of 16 of the 74 refuse collection
employees who were disciplined a year ago for
refusing to work in adverse weather. The
ruling held that city officials were correct
in removing the workers from the payroll for
the half-day on which they did not work. The
commission reported that there was no contention
that the weather or the condition of the
streets furnished a reasonable or proper
excuse for refusal to continue work, but
that the sole issue is whether the employee
actually refused to continue the performance
of his duties. The uspensions of 3 days,
added as a disciplinary measure, were set
aside for 14 drivers and two collectors on the
grounds that city officials had failed to
prove that these employees had refused to work.
65-0134
Efficiency of MPL bulk refuse-system proved.
Public Cleansing, 55(8):485-490, Aug. 1965.
The maximum payload system at Hammersmith,
England, where presently 6,600 tons of the
9,000 tons per 3 months are handled in 3 MPL
vehicles with 14-ton load capacities operating
from one press at the transfer station is
described. Vehicle capacities, refuse loading
and handling methods, labor requirements,
advantages of this system over open hauling,
and the gradual implementation of the system
are explained.
65-0137
Flexibility: Contractor's key to sports arena
collections. Refuse Removal Journal,
8(8):24-25, Aug. 1965.
Fleet Disposal, Inc. services large commercial
and industrial enterprises as well as the
Los Angeles Sports Arena. The firm has 3,000
containers, which enable it to use one truck
with one man per route. Fleet constantly
reviews its collection procedures to insure
efficiency.
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0131-0144
65-0138
Free city collections no bar to contractors.
Refuse Removal Journal, 8(9) :16, 18, Sept. 1965.
When Adams Run Services, Inc., expanded into
the industrial area of Charleston, South
Carolina, it competed against free municipal
collection. But it was successful because of
its use of containers and its adaption of
service to the customer's needs.
650139
Green, L. B. Keep refuse collectors on the
route. American City, 80(6):110-111 , June 1965.
Some routes in Montgomery, Alabama, require
a 23-mile round trip to the disposal site
which has resulted in a 2 to 3 hr time loss.
To provide a high level of service at minimum
cost, officials felt it necessary to keep
collectors on the routes and to buy ten
garbage trains. Each train consists of three
LoDal trailers holding 5 cu yd towed by
a Kaiser Jeep or International Scout. The
trains are used on the ten most southern
routes in the city because they are farthest
from the disposal site. They rented a
storage lot centrally local between the ten
routes and near the freeway. The truck and
train combination has reduced fuel consumption
from between 25 and 30 gal per route to about 10
gal per route.
65-0140
Growing demand for LoDal home train systems.
Western City, 41(7):36, July 1965.
LoDal, Inc. has taken over the former Ford
plant at Kingsford, Michigan in order to keep
up with the demand for LoDal Residential Train
Systems. The train, towed by a Jeep or Scout,
consists of three steel containers, each on
a single axle with pneumatic tires. These
trains rendezvous with a LoDal Transfer Truck,
a high capacity compactor, which alone takes
the refuse to the dumpsite. The City of
Tucson, Arizona with 40,000 stops saved $5,600
a month with this system in 1963.
65-0141
Half of Birmingham 'Dustless'. Public
Cleansing, 55(4):203, Apr. 1965.
About one-half of Birmingham, England's
300,000 homes are now served by a dustless
collection system, using pneumatic can
lifters at the rear of the truck. Special
problems have arisen in the removal of bulk
items with suggested solutions of a special
tray or space for bulky items on the truck, or
separate pickup by request.
65-0142
Haller waste removal trucks at an exhibition
in Munich. Staedtehygiene, 16(3):77, Mar. 1965.
Haller has built a new truck which will
receive and compress even refuse containing
bulky objects. The truck is presently being
tried out in various municipalities. So far
it has proved to be very satisfactory so that
a new series of trucks is being produced with
respective volumes of 10, 14 and 17 cu m.
An obliquely arranged transporting wheel squeezes
the waste through an opening with an average
height of 20 cm into the interior of the truck.
The waste piles up until it reaches the
distribution auger hanging down from the hull
top which spreads out the waste evenly across
the entire loading space. The load is tightly
compacted into a package which can be easily
discharged when the rear part of the truck is
tilted. (Text-German)
65-0143
Jacobson, A. Barges collect refuse in Venice.
Public Works, 96(3):140, Mar. 1965.
Galvanized iron flipper lid cans have been
placed at convenient locations in each street
in Venice. Individuals must put their bagged
garbage into these containers to be carted
daily to central loading points where the
refuse is transferred to motor scows having
closed mechanized dumping systems which dump
their loads at a dumping point near the main
land.
65-0144
Jorgensen, P. J. Barges in Holland haul refuse
to incinerators. Refuse Removal Journal,
8(12):10, 33, Dec. 1965.
Three primary means of waste disposal in
major Dutch cities: incineration, composting,
and landfill are described. There are 15
composting plants operating in the Netherlands.
Some are rasping plants which rotate the .
material by means of projecting arms,
reducing it in size, and separating out
pieces of ferrous metal. The compost thus
produced is generally sold in bulk. Others
are Dano plants, where bio-stabilizers process
the material by passing it through increasingly
27
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Collection and Transportation of Refuse
higher temperatures. The resultant compost is
stored before final disposition is made.
Composting and rasping facilities have not
become objectionable in any manner. In two
composting installations near Copenhagen,
sludge from adjacent sewage treat-nent works
is incorporated into the compost. A special
method of refuse collection prevents direct
exposure to the air.
65-0145
Kampert, W. Collection and removal of liquid
sludge and city refuse. In Refuse and waste
disposal. Berlin, Druckhaus Lichterfeld GmbH,
1964,
Principles of design and operation of vehicles
for the collection and transportation of liquid
sludge and oily refuse are discussed. The
laws and regulations in force, general
requirements, size of vehicles, and types of
drives are included. Collection and removal
of excrement and sludge are discussed.
Sludge-suction vehicles with additional
equipment for cleaning gasoline separators,
vehicles for cleaning gasoline separators,
vehicles for eliminating oil traces and
vehicles used in case of serious oil accidents
are discussed. For collection and removal of
crude and industrial sludge tank vehicles,
sludge-suction vehicles of special design,
and oil-tank cleaning vehicles are discussed.
The organization and costs of collection and
removal of sludge and oil-containing liquids
are discussed.
65-0146
Kildoy, G. W. Refuse train brings three-way
savings. American City, 80(1):88-90, Jan. 1965.
Winston-Salem, North Carolina, has switched
to the train system of refuse collection. The
use of 27 refuse trains and six packer trucks
has produced savings in initial, maintenance,
and operation costs as well as savings from
the elimination of one route. Other
advantages and some disadvantages in using
this system are also outlined.
65-0147
Koukal, R. The City of Zurich introduces
trash ducts in buildings. Schweizerische
Bauzeitung, 83(48):889-891, Dec. 1965.
With the introduction of the transportable
800 liter containers Zurich is now able to
use the trash duct disposal method for
apartment houses, hospitals, etc. It is about
to be installed in two buildings under
construction. Since the installation of a
trash duct in a completed building is often
impossible, it is advisable to plan for it in
new housing projects. Their location must be
carefully selected so that no residents are
disturbed by the noise of trash tumbling
down the duct. The disposal inlets must be
easily accessible and are best installed in
the common hallway of each floor. They must
seal off the duct tightly. The reception
chamber at the end of the duct must agree in
size with the container, must be ventilated,
easily cleanable and must be closed by a
fireproof door. Additional storage room must
be provided for enough containers to hold
all trash accumulating in a week. The bulky
waste which cannot go down through the duct
must go to one or two containers in the
storage room assigned for this purpose.
Special 10-liter trash cans for the kitchen
have been designed which will empty easily
into the duct without jamming it or producing
dust. Details of the construction of the
trash duct and dimensioned drawings are given.
(Text-German)
65-0148
Load lugger makes its bow. Waste Trade
World, 107(16):17, Oct. 16, 1965.
The Telehoist Load Lugger materials handling
system will be displayed and demonstrated for
the first time at the Scottish Motor Show
in Glasgow, Nov. 12-20, 1965. The system is
for basic vehicle chassis up to 22 tons.
Chassis are equipped with a flat-bed platform
and hydraulically operated loading boom,
pivoted at the rear of the chassis platform.
Stabilizers automatically provide support
during loading and unloading and a pivoted
hook engages skips for dumping. All
operations are cab-controlled. The Load
Lugger can handle a variety of materials,
both solid and liquid, in open or closed skips,
also packaged or loose pelletized loads.
The firm claims considerable cost savings
over alternative handling methods, with
savings on labor, maintenance, and licensing
alone paying for the system in less than 12
months. The complete Bedford TK and Load
Lugger system sells at about h3,750.
65-0149
McDonald, J. P. One-man refuse collection.
American City, 80(9):93, Sept. 1965.
A 3 month test, using a modified open truck
and paper system, proved that one-man refuse
28
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0145-0156
collection is possible in College Park,
Maryland. A second-hand mail truck body was
extended to give it a 10 cu yd capacity, and
a hoist was added for rapid unloading. Results
of the test indicated an annual saving of
$17,000. Another factor contributing to the
success of the experiment is the relatively
short distance to the landfill--from 1 to 8
miles, depending upon the collection route
being serviced. The human element probably
presents the most complex problem of the new
system; since the men object to working alone,
increased wages have been proposed to
compensate them.
65-0150
More refuse collected with less work.
American City, 80(7):26, July 1965.
A small 3-wheeler collection vehicle used
for picking up refuse in the sparsely populated
suburban county of Wyandotte, Kansas is
described. The vehicle collects from about
ten homes and then empties directly into
the packer truck, saving an estimated 26
man hours monthly.
65-0151
Municipal departments slowed down by employee
shortages. Refuse Removal Journal, 8(11):34,
Nov. 1965.
City sanitation departments with worker
shortages are trying student workers part-time.
Lower overall waste volume with home garbage
disposal unit requirements are noted.
65-0152
News report.
Oct. 1965.
Staedtehygiene, 16(10):8,
Haller GmbH, Stuttgart, designers and builders
of specialized vehicles, developed a new 10
cu m trash collecting truck. Also new is a
truck for collecting trash from 1.1 cu m
trash containers. Lifting and tilting of the
containers are activated hydraulically. A
novel street cleaning machine holds 2.5 cu m
and sweeps 4 to 15 km per hr at a width of 2.2
m. A water tank holds 600 liters for spraying.
All mechanisms are hydraulic. Only one engine
powers this vehicle which weighs 5.5 tons.
(Text-German)
65-0153
19 miles not too long for Toulon. Public
Cleansing, 55(2):75-78, Feb. 1965.
Toulon, England, now utilizes a landfill site
19 miles from the town. Use of an efficient
transfer station, which gravity fills the
four 53-cu-yd capacity Dumpster trailers
carrying 16 tons a piece, facilitates removal
of 140 tons per day of raw refuse. Use of
articulated trailers at dumpsites is a
problem, and a special tractor with a half-truck
or twin driving axles for constant use at
the site was suggested. The feasibility of
long-distance haulage is shown, and variants
of night haulage are also possible.
65-0154
N. W. Centre members see Oldham's workshops,
discuss transport pool. Public Cleansing,
55(4):223-232, Apr. 1965.
Oldham, England, has instituted a central
transport pool, under the direction of the
sanitation department. Because most of the
145 vehicles serviced were used for refuse
collection and transport, and were also the
most difficult to service, the sanitation
department was chosen to control the pool.
The facilities of the new central workshop,
its policies and organization, reasons for its
institution and its operating advantages are
explained. Be consolidating small municipal
departmtnes into one motor pool, better
maintenance, better repair facilities, better
stocks of spare parts and spare vehicles, and
more variety of vehicles would result. A
brief discussion of pros and cons, particularly
on management of the motor pool is included.
65-0155
One man's burden. Public Cleansing,
55(11) :633, Nov. 1965.
A British Occupational Safety and Health
booklet on maximum permissible weights that
can be carried by one worker is reviewed. A
Geneva meeting of experts advocated vocational
training to reduce lifting accidents and
medical supervision to prevent employment of
those unsuited for lifting. A maximum weight
load of 88 to 110 Ib was recommended for adult
males. The booklet also contains an outline
of National Law and Practice on carrying loads.
65-0156
Packer speeds conditioning in Santa Fe Freight
yards. Refuse Removal Journal, 8(6):8, 18,
June 1965.
The Santa Fe Railroad's repair and conditioning
station in Clovis, New Mexico, has a new
29
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Collection and Transportation of Refuse
refuse collection system, consisting of a
21-cu yd Hobbs Hyd-Pak. The packer enables
a faster and much more efficient clean-up
than was previously obtained by small open-top
trucks and wagons.
65-0157
Paternoster, A. C. Two-wheel traction for
packer body trucks. Public Works, 96(1):78,
Jan. 1965.
The installation of a two-wheel-traction type
of differential on five of the refuse packer
trucks of East Detroit, Michigan, has greatly
minimized stalls and wheel-spinning.
65-0158
Pingeon, E. Use of the Rhone River for the
transport of garbage and residual sludge from
the filtering plant of Aire. Bulletin
Technique De La Suisse Romande, 91 (14):217-224,
July 1965.
As part of a plan to remove solid wastes from
the city of Geneva, a model of the Rhone-Arve
River junction was made in order to determine
the size of tugboats and barges to be used to
haul the solid wastes, as well as the maximum
river flow for safe handling of the barges
(river flow controlled by hydroelectric dam
at Verbois). The loading site of the barges
is at the junction of the two rivers. A
curved section of downstream river bee was
also modelled and the river bed corrected for
better small-craft navigation. Downstream,
the solid waste destruction plant receives the
barges in a canal where an elevator lifts the
barges to the required height for unloading.
The pace of this river traffic is determined
by the needs of the furnaces, which consume
between 200 and 400 tons per day. Reception
silos can hold surplus wastes until the
furnaces can receive them. (Text-French)
650159
Problem of the missing workers. Public
Cleansing, 55(11) :643-644 , Nov. 1965.
Britain is facing an acute shortage of men
willing to staff the street cleansing and
refuse collecting departments. Labor
shortages mean a cutback in refuse collection.
The Reigate Bourough Council were recently
given details of how their labor force has
shrunk. In 1953 the Council had 35 street
sweepers at work. By 1963 the figure had
fallen to 23. Today it is 16. The
unsuccessful effort to recruit more men is
blamed on two major factors--one, that
Britain is enjoying boomtime employment rates
and secondly, that manual workers in local
government are at the back end of the earnings
table. The combination of these factors means
that more and more workers are choosing
factories and their bigger pay packets in
preference to local authority employment.
65-0160
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,
91SA5(1) :17-36, Oct. 1965.
A mathematical, computer-programmed system
for optimizing refuse disposal systems is
explained. The computer simulates variables
in the daily route method of refuse collection
with the following: hours required to
complete the task, frequency of trips to the
disposaj site and distribution of activities
at the site, overall efficiency, truck capacity,
service density, average and variation in
the amount of refuse collected daily, haul
distances, the frequency of service, and the
number of unloading docks at the disposal
site. Applications of the technique include
use in instituting and revising refuse
collection systems, equipment and disposal
sites to make them more practical and economical.
65-0161
Road rail freight container handling.
Cleansing, 55(7):390, July 1965.
Public
The Dempster 'Sideloder' is developed to meet
a growing demand for integrated road-rail
movement of containerized goods. This
Sideloder is highly mobile and can be sent
almost anywhere for unloading or transfer
work, and needs only a single operator.
Railroad flat cars and road delivery trucks
are easily adapted to this innovation.
Prices of Sideloder units together with
chassis are expected to be fcSOOO to E9000,
while converting costs of rail flat cars
would average less than fc200 each.
Development of the Sideloder may lead to the
growth of a new medium for the long distance
hauling of refuse, which appears to be the
only practicable buffer between the absence
of local landfill sites and the relatively
high costs of mechanical disposal. With the
Sideloder, there are substantial reductions
in time and labor, due to the elimination of
handling and reloading.
30
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Disposal-General
collection agencies are discussed. Research
in the field is in the area of systems
analysis. One type of research needed is
data collection, which is discussed fully.
65-0166
Trailers help to solve park refuse problem.
American City, 80(8) :158, Aug. 1965.
To solve its refuse collection problem,
Salisbury Park, a 1,000-acre recreational
facility in East Meadow, Long Island, uses
rubber-tire mounted Dempster Container Trains.
This is necessary, since trucks could not
reach many areas because of narrow trails and
delicate playing turf. The trains., towed by
soft-tire tractor, can travel over delicate
playing-field sod and into hard-to-get:-at
places. To give this system added flexibility
and bigger over-all capacity, larger
capacity-fixed containers were placed at major
accumulation points where they were accessible
to the Dempster-Dumpmaster self-loading packer.
The system of 35 containers, fixed and mobile,
and the one large packer truck has reduced
manpower; more than two-thirds of the
former refuse collection and clean-up crews
could be shifted to other types of work.
65-0167
Truck loader lifts 3600 pounds in beach
cleaning operation. Refuse Removal Journal,
8(5) :26, May 1965.
The 1965 model Beach Sanitizer, powered by a
tractor, can hydraulically lift and dump up
to 3,600 Ib of debris directly into a truck
or trailer.
65-0168
Versatile machine for Barking. Public
Cleansing, 55(3):140-141, Mar. 1965.
A modified truck now in service in Barking,
England, can load and carry an abandoned or
wrecked car, load and carry a standard 6 cu
yd container, or transport small loading
shovels and similar equipment. A brief
description of the modified truck is included.
65-0169
A witch clears the harbor.
80(10):62, Oct. 1965.
American City,
debris from waterways with a hydraulic scoop
that resembles those mounted on self-loading
trucks. Three such vessels are cleaning
up 37 miles of docks in Liverpool, England.
Each of these units has the capacity to
collect 50 ton per day. The 25 ft long craft
can carry up to 1 ton of watersoaked debris
in its tubular steel and mesh scoop measuring
10 by 4 by A ft. One of these dredgers
cleared 3,000 sq yd of oil in less than 3
days after sawdust had been spread to absorb
it. The vessel's 30 hp diesel engine supplies
power for propulsion and for the hydraulic
scoop. It cruises at 8 knots, and works at
4 knots.
DISPOSAL-General
65-0170
Angels adopt a mechanical goat.
80(8):16, Aug. 1965.
American City.
The city of Anageim, California, will include
a $50,000 refuse disposal mechanism which
shreds, wets, and then squeezes a ton of
trash per hr into 20 percent of the original
bulk at the new baseball stadium for the
California Angels. About 13,000 Ib of refuse
accumulate with each ball game.
65-0171
Answers from Mr. Archer.
55(9):515, Sept. 1965.
Public Cleansing
Several questions posed at the 1965 Scarborough,
England, conference on refuse disposal are
answered. Screening of refuse before incineration,
dependent somewhat on other factors, is not
economical with less than about 25 percent
dust. Multi-shift incinerator operation is
generally feasible only in large,
continuous-grate plants. Two hundred ppm
sulfur content is average for British
incinerator smoke.
65-0172
ASME annual meeting highlights--!.
36(8) :49-55, Feb. 1965.
Combustion,
A new diesel-powered surface dredger, named
the 'Liverpool Witch', is skimming floating
Four papers presented at the ASME annual
meeting in New York in Nov. 1964 presented
the following problems: the need for a
common base for evaluating efficiency, capital
cost, solid combustible loss, and availability
of refuse burning systems: the failure to
32
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0166-0176
utilize waste heat; the difficulties in
conventional sludge heating systems; and the
problem of burning rubbish and refuse in
separate furnaces. The object is to present
a summary of the results of papers presented
at the meeting. The state of the art is
indicated in regard to incineration and
industrial wastes. In an attempt to provide
a common basis of comparison of refuse
burning systems, methods are established to
determine the solid combustible losses for
solid fuel units, the stack dust emission
rates, and the reclrculated system loadings.
In the discussion of the utilization of
waste heat from industrial sources, a boiler
conversion is described which would permit
the burning of liquid and solid wastes from
consumer products as well as rubber chemicals
and plastics, together with normal refuse,
such as garbage, rubbish, paper, and wood.
For a waste fuel-oil-fired steam-generator
with 50,000 Ib of steam per hr operating
rate, the conversion cost would be $30,000.
For heating sludge, the hot products of
combustion from sewage gas are bubbled through
the sludge. Burning of large stumps on a
stationary grate while a flow of burning
refuse is maintained past the object. New
ideas in incineration were presented in these
papers.
65-0173
Atomic blasts might help disposal, graduates
hear. Refuse Removal Journal, 8(7):18,
July 1965.
Richard Hamburger of the Atomic Energy
Commission said that a nuclear explosion might
be able to create an enormous cavity
underground where millions of tons of solid
or semi-solid waste could be disposed. He
spoke before the graduating class of the
solid waste course given by Rutgers University.
65-0174
Behrens, G. Experience in the maintenance
and supervision of metropolitan waste disposal
sites. Staedtehygiene, 16(10) .-230-232, Oct. 1965.
It is always rather hazardous to have waste
disposal sites close to residential areas
especially so if the waste is dumped into
abandoned clay pits where the accumulating
rain water cannot drain off. It mixes with
the decomposition water of the waste instead,
which is rich in hydrogen sulfide. Often the
water flows in an open trench to the sewage
canal annoying neighboring residents by its
odors. Quite frequently measures were taken
only after a number of complaints. By
adding chlorine to the water in the pit the
hydrogen sulfide is bound and the odor along
the trench eliminated. Moreover the newly
deposited waste should be immediately covered
with soil. All waste disposal sites must also
be fenced in and guarded to prevent habitual
garbage collectors from removing partly
usable material like furniture, clothing and
half-perished food. Insects, rats, and birds
that gather there in great numbers must be
exterminated to prevent spreading of diseases.
A new rat-killing poison will soon be on the
market. It will be embedded in wax through
which the luring odors can penetrate but
which will not dissolve in the rain.
(Text-German)
65-0175
Boettcher, F. 1965 water technological
meeting in Goettingen. Wasser und Abwasser,
106(36):981-986, Sept. 1965.
The German Association for Gas and Water
Control and the Association of German Gas
and Water Companies held a meeting between
March 11 and 13, 1965 In Goettingen, Germany.
Among a number of papers presented which dealt
mainly with drinking water, waste water, etc.,
one treated the dumping of waste and its
influence on groundwater. It was stressed
that, according to 1961 statistics, 97
percent of the entire waste accumulating
annually in Germany is still dumped and that
deposit sites must be found for 44 million
tons annually. In most cases, not much
attention is paid to where and how the waste
is dumped. A considerable impairment of
groundwater was discovered, mainly through
the increase in mineral salt concentration.
(Text-German)
65-0176
Braun, R. Technical terms and their
explanation. In Refuse and waste disposal.
Berlin, Druckhaus Lichterfeld GmbH, 1964.
A joint committee 'Definitions' of IAM and
AKA have compiled the most important and most
frequently used technical terms from the
field of waste disposal and accurately defined
them. The list is divided into eight sections
in which the technical terms with their
explanations are arranged in alphabetical
order and numbered. A general alphabetical
list of technical terms is provided, which
should facilitate the use of the index. The
eight sections are: general technical terms,
hygiene and microbiology, planning and
33
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Disposal-General
economy, collection and removal, sludge
treatment, dumping, composting, incineration,
and operating and administration.
65-0177
Bredar, W. L. Denver's Metro waste treatment
plant. Civil Engineering, 35(12) :64-66, Dec.
1965.
The new Metro Plant will cost $17 million and
is designed to handle the expected growth
through 1982 of all the member districts. The
primary treatment capacity is 27 mgd to treat
raw waste from the Clear Creek and the Sand
Creek basins. The secondary capacity is 117
mgd to treat all primary effluents plus the
effluent from Denver's existing primary plant.
The activated sludge process will consist
of thickening followed by vacuum filtration,
incineration or drying. Extensive dewatering
procedures required to permit construction
on a 'wet' site are necessary, (The normal
water table is only 11 ft below the surface.)
Five thousand uplift piles have been used to
anchor all deep structures. The entire
complex consists of 14 buildings all faced
with precast aggregate panels with porcelain
trim. The Metro District, organized in May
1961, includes the City and County of Denver
and 12 adjacent municipalities, covers 250
sq m with a population of 800,000, and an
estimated population of 1.5 million by 1980.
The Metro Plant was built by a board made up
of one member from each municipality for each
25,000 of population and provided that no
municipality may have more than 50 percent
of the total membership. At present, there
are 26 members, 13 from Denver and 13 from
the other 12 municipalities. A bond issue
of $32.5 million approved in 1962 is secured
by revenues anticipated from the plant's
operation. The technical details of the
construction, the uplift piling, the use of
the critical path method in the design as
well as in construction, are all described
in some detail. The major suppliers of
equipment are listed and the treatment
processes outlined.
65-0178
Bustamente, R. , H. Davis, and E. C. Fox.
Determining the BOD loading from a zoo.
Public Works, 96(2):121, Feb. 1965.
A Tulane University research project undertook
the determination of zoo animal waste organic
loadings. The primates tested included two
Bengal tigers, a leopard, a cheetah, two lions,
a Kodiak bear, a sun bear, a rhesus monkey,
and a dog-faced baboon. All were males,
except one of the tigers and the cheetah. The
female tiger was a cub and the rest were
adults. The sampling was for fecal matter
only. Each sampling represented a 24 hr
accumulation. The analyses consisted of a
weight determination and a 5-day BOD. A
possible error in weight determination
might have resulted from evaporation, the
cages being open to the weather. To
determine BOD 10 g of each specimen were
thoroughly mixed with 1000 ml of distilled
water, providing a dilution of 1 percent.
The results were tabulated. The BOD of the
feces of the feline animals ranges higher than
those of the primates and bears. The
figures, pounds of BOD per Ib of animal, show
good correlation with each other and with
human waste. Considering the generally used
design factor of 0.17 Ib of BOD per person
and an average weight of 150 Ib, the parameter
would be 0.00113 per Ib. The tests were
admittedly inconclusive in some respects, with
urine sampling omitted and solid content not
fully determined.
65-0179
Carmichael, W. World's largest cleansing
department. Public Cleansing, 55(2):69-74,
Feb. 1965.
The activities of the Tokyo sanitation
department presently serving 10 million
people are described. The central authority
for this department receives about $50
million per year, 4.1 percent of the municipal
budget. Presently, 2/3 of the raw refuse is
landfilled on an island site, and 1/3 is
incinerated in 9 plants in the city. Because
of landfill site scarcity, the city will be
building 10 new plants before 1970 to
incinerate all of its 900 ton per day refuse
collection. The sanitation department also
empties cesspools at night, as only 25
percent of the homes are on sewer lines.
Mention of Olympic games cleaning procedures
is made. Street cleaning is done by 1,100
manual laborers paid at about $1.40 per day.
The department has good techniques and will
eventually match those of other large cities.
65-0180
City waste treatment facilities still needed.
Western City, 41(10):55, Oct. 1965.
According to Richard Pickard, chairman of
the Conference of State Sanitary Engineers,
there are 5,277 communities which need
municipal waste treatment works. The
34
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0177-0184
population of these communities dropped from
36.7 million in 1964 to 33.2 million in
1965. There are 1,342 communities (pop. 11.3
million) discharging untreated wastes into
streams, 1,33/ communities (pop. 16.8 million)
discharging inadequately treated wastes, and
2,598 towns (pop. 5.1 million) in need of
sewage collection facilities. The
construction costs are estimated at $1.86
billion but to eliminate the backlog, the
annual level must rise to $865 million.
In 1964, municipal construction amounted to
$590 million.
Several aspects of American solid waste
disposal are briefly examined from a British
viewpoint. The general level of facilities
in America was not thought superior to those
in England. The American refuse was credited
with a higher percentage of combustibles with
less ash, which favored incineration, than
England. No standardization of vehicles or
methods was noticeable in the United States.
Some open dumps were still used, but much
sanitary landfilling was done, even next to
drive-in theatres situated on top of
completed fills.
65-0181
Connel, J. M. Solving two major problems of
a modern city: a combination garbage
disposal-desalination unit. Heat Engineering,
40(5):64-71, Sept.-Oct. 1965.
Foster Wheeler Corporation's concept
envisages the disposal of municipal refuse
in a water-cooled incinerator and the use
of the steam produced from this process as a
'free heat' source for the flash evaporation
of the seawater which is found in close
proximity to most large cities. The plant
cycle is shown on an accompanying schematic
diagram and indicates the principal equipment
necessary in the overall complex. Each
refuse disposal unit is capable of completely
burning 400 ton per day of municipal refuse
and generating 120,000 Ib per hr of steam.
Large particles of fly ash will be caught
in the boiler hoppers, but the insidious fine
dust is removed within the electrostatic
precipitator. A pictorial representation is
presented of a thirty-two stage, 5 million
gal per day flash evaporator. The evaporator
converts sea water into fresh water by causing
the sea water to absorb heat while flowing
within tubes and then allowing some of that
water to flash into steam from a pool while
under vacuum. Minute salt particles remain
within the pool, while steam condensing on the
outer surface of the tubes and raining into
the trays is pure drinking water. Installed
capital costs of the complete plant with an
operating personnel of 48 is estimated at
$9,700,000. The operating costs of refuse
disposal are estimated at $2.24 per ton
based on 800 ton per 24 hr day for 335 days
per year. Potable water production operating
costs will be $.324 per 1,000 gal based on
a production of 5 million gal per day for
350 days.
65-0182
Davies, A. G. The American way of cleansing
life. Public Cleansing, 55(2):93-94, Feb. 1965.
65-0183
Drobny, N. L. Survey of Antarctic water
supply and waste disposal facilities, practices,
and problems. Technical Note N-708. Port
Hueneme, Calif., U.S. Naval Civil Engineering
Laboratory, Apr. 1965. 24 p.
A survey of water supply and waste disposal
problems at existing U.S. Stations in the
Anarctic is presented. Problem areas are
identified, and potential research and
development efforts are suggested. Large,
small, and inland stations are examined. At
McMurdo, a large coastal station, the disposal
of human waste and garbage is extremely
primitive; 'honey buckets' are used and
emptied in the bay. The construction of a
conventional community liquid water
distribution and water-carriage sewage
collection system is planned for this station.
Waste disposal at Williams Field and Hallett
Station also used a honey bucket system but
no specific improvements are recommended since
these two stations are quite small. The South
Pole inland Station uses 5-gal flush-type
toilets. The waste water from these units
along with that from the urinals and washing
machine is discharged into a pit in the snow.
Other inland stations also discharge waste
to snow. Problems are associated with the
disposal of solid waste to the surrounding
snow such as: health hazards; loss of
structural support due to the creation of
large below-grade cavities; and contamination
of the snow environment. A minimum flush
toilet is recommended for these inland Stations.
65-0184
Duckworth, S. The meterologically scheduled
open burn. Journal of the Air Pollution
Control Association, 15(6):274-277 , June 1965.
The feasibility of scheduling open burning
(such as that now prohibited under Regulation
I of the Bay Area Air Pollution Control
35
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Disposal General
District at San Francisco) under selected
meteorological conditions is discussed. Tables
given include various indicators of pollution
potential and a theoretical calculation of
airborne particulate material in half-plume
cross-section at two downwind distances. A
photograph shows the effects of firing a
poorly stacked 40-ton pile of debris. One
graph shows a mathematical estimate of
visibility reduction from the open burning of
28 tons of brush at various distances. The
latter shows an opaque plume at 300 ft and a
Ringelmann No. 1 at 2,000 ft. Another plot
shows the fallout pattern isopleths from the
open-burning of 300 tons of land-clearing
debris. Requests for variance from Regulation
I have been based on the applicant's willingness
and his consultant's ability to schedule a
proposed open-burn under meteorological
conditions favorable for the dilution and
travel of the resulting airborne pollutant
cloud. Meteorologically scheduled open-burning
offers a feasible way for single disposal
of land-clearing debris under the following
conditions: the economic saving is large and
other methods of disposal are not readily
available, the site is remote from populated
areas, the debris is dry, well-stacked,
and fired in competent supervision, and the
community is willing to accept the esthetic
loss on the day of the burning.
65-0185
Dump owners move to cut air pollution. Refuse
Removal Journal, 8(6):32, June 1965.
An East St. Louis city engineer reported that
some industries have held up plant expansion
in an area north of the city because of the
smoke nuisance from burning refuse at six
open dumps. The open dump operators, whose
burning is charged with adding to air pollution,
were ordered to extinguish their fires and
find more suitable refuse disposal methods.
Representatives from five of the six operations
are taking steps to end the fires and comply
with the Illinois Air Pollution Control Act.
A preliminary hearing found the dumps were
contributing to air pollution and they were
ordered to halt burning. Later the board
granted an extension until more hearings were
held. Since then, health officials have
observed dense smoke coming from all the dumps.
Two of the cities involved have studied the
feasibility of an incinerator as a joint
venture, whereas another city intended to
use sanitary landfill because it could lot
afford the $350,000 needed for an incinerator.
Two of the thiee private dump operators
explained that they had just purchased
equipment which would allow them to begLn
sanitary landfill operations, and thus comply
with the order.
65-0186
Dump smoke causes asthmatic outbreak. Refuse
Removal Journal, 8(1):28, Jan. 1965.
Smoke from an abandoned city dump burning
underground was the first air pollutant linked
to asthmatic outbreaks in New Orleans, Louisiara.
The dump is located in the north-east
section of New Orleans, one of two regions
of the city specified as probably emanating
points of air pollution. A poor combustion
product containing silica was found to be
present in increased concentrations when
peaks in asthma attacks occurred. Skin tests
using smoke extracts produced a very high
incidence (83%) of positive reactions among
victims of previous outbreaks. The outbreaks
are associated with low velocity winds coming
sometimes from the north and north-east.
65-0187
Dunkers, K., and W. Schwalbenbach. Experiments
on dehydrating material retained on a trash
rack at the purification plant Akeshov,
Stockholm. Staedtehygiene, 16(9):193-196,
Sept. 1965.
Experiments with a special type of press
were conducted for dehydration of material
retained on a trash rack at a purification
plant. The material had a high water content
(about 87%) and was thus difficult to
transport to a composting or incineration
plant. The press which was used for
dehydration consisted of two plates which were
operated by two separate hydraulic cylinders.
After a compacting period of about 2 minutes
the press plates were removed automatically
and the dehydrated material fell into a bag.
The weight was reduced by 67 percent and the
volume by 80 percent. An automatic packing
machine was attached to the press which
wrapped the dehydrated and compacted material.
The water left over from the pressing process
was returned to the purification plant. The
compacted material had a solids content of 40
percent in contrast to 13.3 percent before
treatment. Illustrations of the press and
the wrapping machine are given. (Text-German)
65-0188
Effect of solid waste dumping on surface and
underground water. Public Cleansing,
55(10) :575-576, Oct. 1965.
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0185-0191
A summary of Dr. Ing. Wilhelm Langer's paper
presented at the 1965 Third Congress of the
International Research Group on Refuse
Disposal at Trento, Italy is presented.
Types of water infiltration of solid waste
dumps are discussed. General and bacteriological
pollution and factors determining their
persistence in the water supplies are also
presented. Testing for and determining
amount of pollution is explained, and also
ways of preventing pollution.
professional engineer should design sanitary
landfills after thorough study of the site
to assure adequate safeguards to prevent
saturation of the fill either by percolation
or intimate contact with ground water.
Consolidation of landfill sites on an
area-wide basis would produce economies in
operation. The County should establish
criteria to guarantee the minimum public
health standards establish by the State after
the elimination of open dumps.
65-0189
Eldredge, R. W., and H. J. Dominick. 1963-1964
Refuse disposal study, Winnebago County,
Illinois. (1965] 39 p.
Winnebage County, Illinois Js about 91 miles
northwest of Chicago. Rockford, the county
seat, is an industrail city employing most of
the residents of the County who are employed
in manufacturing activities. By 1970 the
population of the County may be about
300,000 with Rockford having about 200,000.
The problem of refuse disposal is compounded
not only by the rapid increase in household
units but also by the increasing amounts of
refuse generated by each unit. The present
study describes the methods of refuse disposal,
gives a brief history of Rockford's refuse
disposal, evaluates the existing solid waste
disposal facilities in the County, and
investigates possible ground water pollution
by sanitary landfills. Conclusions and
recommendations are given in the Introduction.
There is a 10-item bibliography on page 39.
65-0190
Eldredge, R. W., and H. J. Dominick.
Introduction. 1963-1964 Refuse disposal
Qtnrlv. Winnphflpo f.ountv. Illinois.
study, Winnebago County, Illinois
p.1-3.
1965] ,
Winnebago County, Illinois is about 91 miles
northwest of Chicago. Rockford, the county
seat, is the largest city and by 1970 may have
a population of 300,000. Although 83 percent
of the County is farm land, 64 percent of the
population now lives in Rockford. The
problem of refuse disposal is increased by
the growing population and the additional
amounts of refuse generated by each individual
household. The conclusions and recommendations
resulting from the entire study are summarized
in the Introduction. Adequate landfill sites
are needed within easy hauling distance of
all portions of the County. Incineration
should be considered when landfill sites
become more difficult to obtain. A registered
650191
Eldredge, R. W., and H. J. Dominick.
Alternative methods of refuse disposal.
In 1963-1964 Refuse disposal study, Winnebago
County, Illinois. [1965] p.4-15.
Six methods of refuse disposal, their
limitations, advantages, and disadvantages,
are discussed and their use in Winnebago
County cited. Garbage, which accounts for
less than 15 percent of the total refuse
generate^1, may be disposed of by feeding it
to pigs. All states require that such garbage
be cooked to destroy the virus of Vesicular
exanthema and this requirement has reduced
the economic advantages of feeding garbage to
hogs. There are no known piggeries in the
County. Open dumping is the most usual
method of solid waste disposal in the County.
Some are periodically consolidated and
compacted and are therefore less objectionable
than those not maintained regularly. Open
dumps in urban areas can be converted to
sanitary landfills to reduce nuisances,
eliminate public health hazards, and improve
the appearance of the site. The public,
unfortunately, associates all disposal
operations with open dumps, and this makes it
difficult to get sites for sanitary landfills.
Sanitary landfills are economical, with low
initial investment and with operating costs
one-third to one-hald in the cost of
incinerating. They are flexible to adjust
to changes in population and in kinds of
refuse. If refuse has been collected
separately from garbage, sanitary landfill
operation will permit combined collection
with resultant lower costs. The length of
haul can be reduced since sanitary landfills
can be close to populated areas without
nuisance. Sub-marginal land can be reclaimed
and used for airports, parking lots, parks,
playgrounds, etc. The hazards of open dumps
are eliminated. The operation of a sanitary
landfill is described and the disadvantages
listed. The advantages and disadvantages of
incineration are listed and costs given.
Composting and on the site disposal (garbage
grinding) are also discussed.
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Disposal General
65-0192
Eldredge, R. W., and H. J. Dominick. Brief
history of refuse disposal for the city of
Rockford. In 1963-1964 Refuse disposal study,
Winnebago County, Illinois. [1965]. p.15-17.
In 1945, Rockford, Illinois, which was then
a city of 90,000, had 196 cases of polio and
14 deaths. A public demand arose for the
abandonment of the private contract method
of collecting refuse with open tarpaulin-covered
trucks, disposing of garbage by feeding it
to hogs, and disposing of other solid wastes
at an open dump. A bond issue for about
$250,000 was approved and a survey made of
methods. This report, dated October 1, 1946,
is quoted at some length. Sanitary landfill
was suggested as the best solution.
constructing sanitary landfills anywhere withii
the county. Of the eight refuse disposal site;
now in use not one is located in areas
indicated as favorable by the Survey. Only
two provide cover material that in any way
diverts surface water. Six have no barrier
to water absorption, percolation, and possible
water pollution. Two sites have municipal
wells on their periphery. Both wells were
drilled with the knowledge of the disposal
site's existence. The apparent indiscriminate
location of refuse disposal sites has not
resulted, paradoxically enough, In widespread
complaints of water pollution. Perhaps too
much stress has been put on the underground
pollution potential. Adequate safeguards are
necessary, however, to protect the underground
water supply.
65-0193
Eldredge, R. W., and H. J. Dominick. Appraisal
of existing Winnebago County solid waste
disposal facilities. In 1963-1964 Refuse
disposal study, Winnebago County, Illinois.
[1965]. p.17-20.
Visits were made to all the disposal sites
in the County and the technical details of
the present operation are reported.
Recommendations and suggestions are made.
For example: the Rockford Land Reclamation
Site serves the City of Rockford by contract
collection and is available, on a fee basis,
to other haulers. The sanitary landfill is
maintained in better than average condition.
The incinerator's small capacity makes its
operation uneconomical. The City of Rockton
operates a dump on the South Bluff Road
between the road and the Rock Rtver. Garbage
is disposed of at the toe of an open dump
face. This is an eyesore and public health
hazard. The dump should be compacted and
convered. Eight such sites are described in
this manner and the characteristics of each
set forth.
65-0194
Eldredge, R. W., and H. J. Dominick. Possible
ground water pollution by sanitary landfills.
1963-1964 Refuse disposal study, Winnebago
County, Illinois. [1965]. p.21-28.
The Illinois State Geological Survey has
prepared a report using studies of the
geology of Winnebage County, boring records,
water well records, and the general knowledge
of staff members as to the geology and
geomorphology of the area. The report leaves
some doubt as to the practicability of
65-0195
Ellis, H. M. Influence of dumps of solid
domestic and industrial refuse on surface and
underground water - British research and
practical experience. Public Cleansing,
55(6):378-380, June 1965.
Results of experiments on water pollution
from wet and dry refuse dump pits are
explained. The dry dump, with 90 tons of
refuse dumped 5 ft deep and covered by 1M ft
of top soil, was observed for 2'< years under
a rain fall of about 25 in per year. A high
degree of pollution in the percolate was
measured for the first 12 months, after which
contamination rapidly decreased. One hundred
tons of loose refuse was wet-dumped
intermittently over 15 months in a pit of tap
water. Bacterial pollution was originally
very high, but for successive dumps the
heavy initial pollution of various types
created anaerobic conditions which lowered
bacteria concentrations. The results of the
experiment led to careful selection of
dumping sites, and construction of a
purification system for effluent from the
site, using settling tanks, hydrated lime,
percolation, filtration, and aeration methods
together.
65-0196
Erhard, H. History of city sanitation. In
Refuse and waste disposal. Berlin, Druckhaus
Lichterfeld GmbH, 1964. p.1-11.
The problem of waste disposal first arose when
man gathered into tribes in the Indus Valley
managed to solve waste disposal effectively.
Excavations of Mobondscho-Daro and Harappa
have revealed a remarkably high level of
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0192-0200
residential culture. Clay pipes with flanges
led the domestic sexrage to a main sewer in
the street which was covered with hricks or
stone plates. Greeks and Romans also had
water and drainage systems. In 1609 the
municipality of Paris introduced a
street-cleaning service whose costs were
covered by puhlic funds. One of the
indisputable achievements of the British was
their realization of the relationship between
hygiene and martality. It was only in the
2 Oth century that deveoopments took on a
systematic character. Street cleaning was
mechanized to an increasing extent. The first
garbage incinerator was constructed in 1976.
In England, where the garbage had a high
calorific value, incineration presented no
particular problem so that the number of towns
that chose this method rapidly increased.
On the continent, the first incinerator was
built in Hamburg in 1893. Composting the
oldest process known for the agricultural
utilization of urban refuse is also discussed.
650197
Fairlie, P.O. So much rubbish. Public
Cleansing, 55(3) :149, Mar. 1965.
The contents of ordinary waste paper containers
have changed significantly in the past few
years. Not many years ago 70 percent of
household refuse consisted of dust and ashes.
The change over from single dwellings and
household fires to complex apartments with
central heating has changed the composition
of waste to substantial amounts of metals and
bottles as well as the paper or cardboard
refuse used in packaging. New packaging
materials, such as plastic, have created a
serious problem of disposal as they do not burn
down, decompose, or have any use in composting.
As a result of these changes, the bulk of
refuse has increased by at least 50 percent,
leaving officials with two major problems:
(1) the disappearance of dumping sites, and
(2) the difficulty of obtaining proper
decomposition results. Possible solutions
for these waste disposal problems include
incineration and salvage operations.
650198
Garrett, R. Refuse reflections, Public Works,
96(12):128, Dec. 1965.
Refuse disposal has been one of the most
difficult municipal problems because of a
tendency to delay a decision as to which is
best: controlled, open-burning dumps,
sanitary landfills, composting plants, or
incineration plants. A temporary method
only delays and makes more difficult the
final decision. The 'open dump' is not
advisable, although 25 percent of American
cities still make use of it. It is a smelly,
smoky eyesore that decreases land values and
creates nuisances. It is a breeding ground
for rats, insects, and isease. Although it
was the first convenient means of refuse
disposal, it should not be considered in view
of the present disposal crisis.
650199
Hart, S. A. Our wastrel world. Agricultural
Engineering, 46(12):684-685, 691, Dec. 1965.
The wastes created by society and their
disposal are discussed. Two ways to dispose
of wastes are: (1) conversion into usable
material, for example, using manure as
fertilizer; and (2) by discharge into the
environment. Pumping sewage (either treated
or untreated) into a river is an example of
the second method. Making wastes less noxious
before discharge into the environment is not
sufficient. Our rapidly expanding population,
our increased per capita volume and strength
of wastes, and our increased fastidiousness
and demand for more pristine surroundings,
all demand that we do more than merely dump
wastes. We must evolve schemes for the
conversion and utilization of wastes. The
fragmentation of wastes production, wastes
management, and wastes discharge, is a most
serious impediment to solution of the total
problem. The waste problem will not be
solved by such an approach. Solution will
come only through consolidation of attack and
attitude on the total but diverse wastes of
the whole society. Liquid, solid and gaseous
wastes from agriculture, industry and the
municipality, and their insult through discharge,
or conversion, upon the environment resources
of land, water, and the atmosphere, must be
integrated. We are approaching an era when
management science will be an equal partner
in the solution of wastes problems. Computer
techniques will be used to determine what
wastes need to be treated in what manner and
to what degree, and what share of the total
pollutional burden can be shared by the land,
water, and air resources of a community.
65-0200
Jager, B. Types of waste. In Refuse and
waste disposal. Berlin, Druckhaus Lichterfeld
GmbH, 1964.
Types of liquid waste are discussed including
domestic sewage, domestic sewage sludge,
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Disposal-General
sewage from trade and industry, sludge from
trade and industry, oil-containing residues,
and radioactive residues. Types of solid
waste are discussed including domestic refuse,
refuse from trade and industry, waste from
cattle yards and slaughterhouses, street
litter, other refuse, and radioactive waste.
When industrial sewage residues are precipitated
together with domestic sewage sludge, they
may greatly disrupt further treatment of the
sludge due to their special physical or toxic
properties. When radioactively contaminated
residues are deactivated, concentrates
requiring special treatment are formed.
65-0201
Jersey to smother 7-year dump fires. Refuse
Removal Journal, 8(6):20, June 1965.
A golf driving range in the meadows near
Rutherford, New Jersey, had to issue 'smoke
checks', similar to baseball rain checks,
because smoke and fumes from nearby dumps
drove patrons off the range. Now, the
smoldering fires in the East Rutherford flat
lands opposite New York City that polluted
air since 1959 have been snuffed out. The
State of New Jersey allocated $10,000 for the
task, which cauld not be accomplished with
municipal heavy equipment, such as bulldozers
and fire truc'-cs because of the marshy land.
The job was tackled with only hand labor using
water, bicarbonate of soda and clean landfill.
Many of the fires burned underground, fed by
repeated applications of flammable landfill.
The smoke and fumes would offend the eyes and
noses of area residents and would often combine
with morning fog to bring commuting traffic
in New York City to a standstill.
65-0202
Johnson, L. B. Natural beauty of our country.
H. Document No. 78, Congressional Record—House.
Feb. 8, 1965. 12 p.
Continuing technological progress and
improvement in methods of manufacturing,
packaging, and marketing of consumer products
has resulted in an ever mounting increase of
discarded material. We need to seek better
solutions to the disposal of these wastes.
The President recommended legislation to: assist
the states in developing comprehensive programs
for some forms of solid waste disposal;
provide for research and demonstration projects
leading to more effective methods for disposing
of or salvaging solid wastes; launch a
concentrated attack on the accumulation of
junk card by increasing research in the
Department of the Interior leading to the use
of metal from scrap cars where promising leads
already exist.
650203
Katz, P. Problems of waste disposal in the
area of Basel, Switzerland. Schweizerische
Bauzeitung, 83(25) :437-447, June 24, 1965.
There are mainly three methods for eliminating
the various kinds of waste such as household
wastes, industrial waste, sludges, slag,
rubbish, etc. Orderly dumping is one method
but it is now more and more restricted by
hygienic regulations. Dumping into abandoned
gravel or sand pits is prohibited. A layer
of clay, at least, must seal off the
decomposition water from the groundwater,
Every load of waste dumped must be covered
with a layer of soil or sand. Another method
is composting which converts organic wastes
into humus. The composting process takes
place either in rotting beds or in tanks.
The waste layers have to be turned over
frequently. Whether rotting in tanks is a
faster process is still a controversial issue.
The third method of waste disposal is
incineration. The great number of incinerators
now available can be classified according to
size, or type of grate, or continuous or
discontinuous operation. There is no unique
answer to the question of advantages of
incineration over composting. In Switzerland
incineration is preferred since compost has
only a limited market. None of the methods
can ever be considered as profit-gaining
business. The elimination of waste must be
viewed rather as a hygienic and aesthetic task
which must be solved as economically as
possible. The waste disposal situation in
and around Basel, characterized by an acute
shortage of dumping sites, is discussed in great
detail. The problems are compounded by large
quantities of industrial waste from the local
chemical industry. A new incinerator plant
for 600 tons per day (1,200 at a later stage)
is in the planning stage. Its layout is
illustrated and a detailed description of its
construction is given. The plant will serve
44 communities in Switzerland, France and
Germany. Heat will be supplied to a
remote-heating system. (Text-German)
65-0204
Kaupert, W. Third conference of the
International Work Group for Waste Research.
Staedtehygiene, 16(10):233-236, Oct. 1965.
The third conference of the International
Work Group for Waste Research, held May 24
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0201-0207
to 29, 1965, in Trient, Italy, was concerned
with sanitary landfill, methods for cleaning
flue gases escaping from incinerators,
crushing of waste, and composting. A
delegate from the Netherlands reported on
experiments with a two-stage composting
method. In the first stage the material is
spread over rotting beds only 45 cm in height
where a rotting process by mold fungi takes
place. A 3 to 4 week period of post rotting
follows. A delegate from Geneva, Switzerland,
discussed the odor problem in the composting
process. After a number of experiments it
was found that the best solution is filtration
through the soil. Sandy soil proved to be
better than clay. In conclusion, the sewer
sludge problem and waste elimination in Italy
were depicted. Italy is presently at the
stage of introducing sanitary landfills.
(Text-German)
65-0205
Location of refuse disposal sites. Wasser
und Abwasser, 106(8):233, Feb. 26, 1965.
This is a report on an article bv F. Heigl
(Informationsblatt, No 22, International
Arbeitsgemeinschaft fur Mullforschung, IAM,
Zurich). Refuse disposal sites must be
carefully selected in order to avoid pollution
of the groundwater. Diluvial and alluvial
sediments are unsuitable for dumps.
Investigations in the area of the Traun river,
Austria, showed that a groundwater current of
several Kilometers in width flows parallel
to the Traun with only a speed of 1.2 cu m per
second while the annual precipitation is
6,000 cu m per hectare of 0.2 liters per second.
Although a considerable amount runs off on
the surface, enough water penetrates, carrying
with it traces of organic substances which
are sufficient to spoil the groundwater.
Drainage, filtration, and other modifications
of disposal sites are briefly discussed, as
is the location of wells. (Text-German)
65-0206
McCarthy, F. Public cleansing in Great
Britain. Public Cleansing, 55(5) : 300-312 ,
May 1965.
A paper presented by the president of the
Institute of Public Cleansing in Britain to
the American Public Works Association on
general British refuse disposal services is
reported. It describes the criteria for the
changing pattern of British Local government
to regional councils of larger area, explains
the training necessary for executive cleaning
positions, relates services of the Cleaning
Institute, and gives an analysis of British
refuse, pre-war and present, explaining
present high paper and metal can rate and
power cinder content. The standard for
collection systems are expendable or
easily-cleaned receptacle, and refuse covered
from home to dump site. Although presently
galvanized steel cans with detachable lids
are used, the more hygienic dustless and
paper sack system are gaining favor. Plastic
containers are also being tried because of
cheapness, lightness, and quiet operation.
About 80 percent of Britain's refuse is
placed in sanitary landfills, 16 percent is
incinerated, and 4 percent composted. Increasing
haul length of 15 to 25 miles has brought
emphasis on incineration. A variety of
transfer stations are discussed including the
MPL system with static ram compressors and
loader. Comments on composting, on-site
disposal, street cleaning, the Garchey system,
anH gully emptying are included. Continued
progress in Britain's public cleansing field
from larger authority, higher standards,
research, increased mechanization, and land
shortage is expected.
65-0207
McKinney, R. E., and H. H. Benjes. Evaluation
of two aerated lagoons. Journal of the Sanitary
Engineering Division, American Society of
Civil Engineers, 91(SA6):43-55, Dec. 1965.
One new wasterwater treatment system that
has been developed and is currently being
field tested is the aerated lagoon. Originally
the aerated lagoon was tested on industrial
wastes. The results indicated that it should
have value in treating domestic sewage. This
study was carried out to evaluate the usefulness
of aerated lagoons in treating domestic sewage.
It was necessary to measure the flow on a
continuous basis, the power used, the
influent and the effluent characteristics,
and the mixed liquor characteristics. The
operational data include 5-day BOD uptake
rates. Regular microscopic examinations were
made to determine the nature of the
microorganisms in the systems. Basic theory
indicated that aerated lagoons could operate
either as a completely mixed biological
system, lending itself to a relatively simple
mathematical analysis or as an incompletely
mixed system which defies any simple
mathematical analysis. The most efficient
lagoons systems studied required from 1/5 to
1/4 hp per 1,000 cu ft to create complete
mixing. It appears that the oxygen transfer
characteristics of the mechanical, turbine
aerators do not warrant design beyond 1.5 Ib
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Disposal General
o'xvgen mg per liter. The aerated lagoons
yielded 63 percent BOD reduction with 1.7
days aeration system should yield better than
' 50 percent BOD decreases as the temperature
decreases, with lower treatment efficiencies
in the winter.
65-0208
Master plan for refuse disposal. Public
Cleansing, 55(10):570, Oct. 1965.
The 20 year disposal plan of Orange County,
California, is outlined. Presently over
700,000 people produce 2,300 tons of refuse
daily, and an estimated 2,000,000 people will
produce 4,500 tons per daily by 1980.
Disposal is at 3 landfill sites, with about
1/3 of the refuse passing through the 3 transfer
stations. Disposal cost is about $0.70 per
ton.
65-0209
Ostertag, H., and W. Junghans. Use and
elimination of disposable linen in hospitals
and convalescent homes. Staedtehygiene,
16(10):213-218, Oct. 1965.
Disposable linens and diapers are very
reluctantly used because of the high costs
involved. Their price is about 2 or 3 times
as high as that of the conventional washable
and re-usable linen. However, they are more
hygienic and they relieve the nurses of
their most unpleasant work, especially since
the introduction of Moltex diapers. The
used disposable linens are collected in large
paper bags, together with the other hospital
wastes, and are incinerated. The danger of
spreading infectious disease would be too
> great if they were dumped. The wet diapers
and those containing excrements posed some
incineration problems since they did not
fully burn down. Experiments were done in a
pyrometric cone incinerator to find a method
which would thoroughly burn this type of waste.
The full paper bags were loaded into the
incinerator one by one at intervals of 1 to
3 minutes at a temperature of 800 C. The
incineration process was observed through
observation ports in the furnace wall. The
waste burned down fully and the ash residues
consisted only of metal and glass components.
The construction of the furnace is described
in detail. (Text-German)
65-0210
Out-of-staters drop 9,000 yards per day.
Refuse Removal Journal, 8(1):27, Jan. 1965.
About 400 refuse collectors from New York
dump their refuse in New Jersey. New Jersey's
dumping sites are popular because New York
raised its dumping fees.
65-021 i
Refuse analysis at Middleton. Public
Cleansing, 55(12):683-685, Dec. 1965.
A detailed, tabled analysis of refuse from
homes of different classes in Middleton,
England is presented. Refuse content and
densities are analyzed in the tables according
to class of homes. Full incineration is being
contemplated due to the grave shortage of
landfill space within the borough.
65-0212
Refuse disposal at the source. Public
Cleansing, 55(1):12-13, Jan. 1965.
The English ministry of housing is examining
on-site disposal and reduction methods for
multiple dwellings. A letter from the head
of New York's Department of Air Pollution is
quoted in part. It recommends the use of
larger, more efficient municipal incinerators
instead of the small, poorly operated and
maintained, hard to staff, on-site incinerators.
65-0213
Rich, L. G., W. M. Ingram, and B. Berger.
Waste disposal on space craft and its bearing
on terrestrial problems. Public Health
Service Publication No. 999-WP-29. Cincinnati,
U.S. Department of Health, Education, and
Welfare, Aug. 1965. 14 p.
Manned space missions of extended duration
will require regenerative systems that provide
the physiological necessities of man. There
must be a utilization of waste products in
a regenerative process. Solid and liquid
human wastes will be processed to provide
inorganic nutrients for the photosynthetic
component of the system. Two processes hold
particular promise for this purpose. One is
wet combustion, which is an oxidation under
pressure of organics in a water solution or
suspension. Oxygen would be supplied by the
injection of compressed air. The other process
would be an aerobic, thermophilic, microbiological
process. It would be continuous and completely
mixed. A large recirculation ratio would be
used, and the microorganisms in the
recirculated flow would be destroyed thermally.
This process could have application in many
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0208-0216
other fields. Tables, charts, and mathematical
formulas support the facts presented.
65-0214
Rickles, R. N. Waste recovery and pollution
abatement. Chemical Engineering, 72(20):133-152,
Sept. 27, 1965.
In the tragedy of the pollution of U.S. fresh
water and air, industry is only one of many
contributors, such as outdated municipal
sewage systems, automobiles, incinerators,
generators, and the economic advantage of
dumping wastes directly rather than using
waste recovery methods. The techniques of
waste treatment which are available are
described on the premise that in the near
future, antipollution regulations will make
methods, which today are rejected because of
expense, a necessity. General methods of
treatment of liquid and gaseous wastes and
techniques for separation of solids are
discussed. Special problems of the chemical
process industries and the disposal of
chemical wastes are considered in detail with
examples. The general approach to each of
the problems is that the application of the
method requires an understanding of the
method, its limitations, and the nature of
the waste. It is recognized that while some
methods are suitable for recovery of waste
products, many others are final disposal
techniques which preclude recovery of any
wastes except water and heat. The data
included should be a guide to source material
on governmental activities, the state-of-the-art,
examples of techniques in waste disposal
and recovery of by-products from industrial
effluents.
650215
Shults, F. S. Refuse disposal: survey in
prophecy. Public Cleansing, 55(1):39-62,
Jan. 1965.
A survey of England's present solid waste
disposal methods and a look ahead to future
methods are presented. Long-range planning
was cited as the key to efficient waste
disposal. All refuse disposal is by either
'controlled tipping' (sanitary landfill) or
by incineration. Trend in the characteristics
of garbage is to lighter (about 300 Ib per cu
yd 25 years ago) and higher calorific value
(presently about 6000 Btu per Ib). Increase
of hauling distances to 15 to 25 miles greatly
increases disposal costs. Pulverization was
considered only a half-measure, as it only
reduces the volume. Composting was considered
impractical because of trends towards lower
percentages of compostable materials in refuse
and a lack of market for the compost. Bulk
haulage by road farther than 8 to 12 miles
seems impractical. Haulage by rail or water
has been little researched. On-site
incineration was hard to control by untrained,
part-time operators. Large initial investments
for an overall cheaper per-ton disposal
method were usually substituted by lower
initial investments with higher per-ton
disposal costs. Charts showing different
cities' methods and disposal costs are
included. The use of modern, moving-grate
incinerators, coupled with power or steam
production, for most municipalities on a
regional basis, using skilled and semi-skilled
labor is recommended. The use of sanitary
landfills should be restricted to the more
rural and county areas with suitable sites
nearby.
65-0216
Solid wastes. In Restoring the duality of
our environment. Report of the Environmental
Pollution Panel, President's Science Advisory
Committee. Washington, U.S. Government Printing
Office, Nov. 1965. p.134-156.
The many problems of solid wastes are
discussed. They include: sewage, trash and
garbage, auto hulks, and demolition. The
committee points out: (1) The magnitude of
the problem with a statistical evaluation of
all solid waste generated in the United States
from 1959 to 1964; (2) The nature of solid
wastes; the overall nature of the problem is
such that attention should be given to (a) the
improvement of organization and systemization
of the waste material outflow portion of our
consuming society, (b) the improvement of
technology dealing with this outflow and
with the separate steps of collecting,
processing, and disposing, (c) the adoption
of practices and policies that will close the
loop between the materials consumption and
the waste production parts of our society so
that decisions relative to consumption will
consider the waste product problem; (3)
Salvaging and reclaiming; wastes of various
types are recovered each year at an estimated
value of five to seven billion dollars
annually. Copper, lead, and aluminum as well
as scrap iron are salvaged by the millions of
tons each year; (4) Organization and
sociological problems; there is a lack of
awareness that extends from public leaders to
our universities, of the intricacies of waste
management problems. There is a large problem
of local self-education; (5) Technology;
recent potential improvements are cited, such
43
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Disposal General
as (a) sanitary landfills, (b) incineration,
(c) composting, (d) water carriage of solid
wastes, (e) compression and capillary drying
techniques; (6) Automobile hulks; some
research programs are in progress to find
uses for auto hulks other than as scrap steel.
Some possibilities are (a) design automobiles
so they can be more easily cannibalized, (b)
increase the interchangeability of automobile
parts, so that the junk car might be
cannibalized more rapidly for its parts, (c)
improve the salvage process by a rerversal of
'production line' technique, including the
economics of super-scale entralized scrap
yards, (d) consider the reconcentration of
automobile hulks, in effect building an
artificial iron mountain as a future resource,
(e) institute a clean-up train which would
collect, dismantle and compress junk cars
in remote places.
65-0217
The sources of pollution. In Restoring the
quality of our environment. Report of the
environmental pollution panel, President's
Science Advisory Committee. Washington, U.S.
Government Printing Office, Nov. 1965. p.10-11.
The pollution sources, municipal and industrial
sewage, animal wastes, urban solid wastes,
mining wastes, consumer goods wastes and
unintentional releases are described. Sewage
effluents, whether or not treated, carry
considerable quantities of phosphorus,
nitrogen, and other plant nutrients and are
a principal source of the damaging
overfertilization of rivers, lakes, and
estuaries. Excreta of farm animals are a
major source of water pollution. Odor and
fly problems arising from waste accumulations
are acute in the feedlot of beef cattle and
the mass production of poultry and are made
more critical by encroachment of suburbs into
what were farming areas. Estimated annual
output of urban solid wastes, containing
paper, grass and brush cuttings, garbage,
ashes, metal and glass, is 1,600 Ib per capita.
Currently this means 125 million ton per year,
whose collection and disposal costs about
$2.5 billion a year. In the United States
during 1963, more than 3.3 billion tons of
waste rock and mill tailings were discarded
near mine sites, also vast mountains of slag,
ash, and other waste material. The billions
of tons of consumer goods wastes are also
discussed statistically, as are unintentional
releases.
65-0218
Stirrup, F. L. Assessing disposal methods.
In Public Cleansing; refuse disposal. Oxford,
The Institute of Public Cleansing, 1965. p.11-15.
Disposal methods must be analyzed for their
aspects. One must consider the composition
of the refuse; technical resources and land
available; dangers to health, waterways, fish
hatcheries; amenity; future development; capital
and operational costs; distance; and practical
and economical utilization of materials. If
near farming area, compost would be useable.
Steel mills want scrap metal. Paper and
fibreboard manufacturers can use refuse. It
is important to consider extreme climatic
conditions of heat, cold, rain, or fog.
650219
Stirrup, F. L. Refuse composition. In Public
cleansing; refuse disposal. Oxford, The
Institute of Public Cleansing, 1965. p.4-10.
In Great Britain domestic refuse Ln analyzed
with the object of obtaining data as to yield,
composition, and seasonal variation. The
temperature and rainfall are recorded; the
vehicle carrying test load is weighed. Refuse
is passed through a screen to extract dust
and cinder. The weight and percentage of
each type of refuse is analyzed. Dust contains
a small percentage of coal residue, but is
mainly the result of complete combustion of
solid fuel on domestic fires. It is largely
mineral in character. Cinder is useful as
a low grade fuel for heating installations.
Vegetable and putrescible matter are used in
compost preparation and for fertilizers.
Paper can be recovered and repulped for use
in manufacture of fibreboard and low grade
paper. Metals are saleable. Rags may be sold
for making new cloth, roofing felts or in
linoleum manufacture. Glass must be well
cleaned and sorted into white or colored to
be saleable. Crude refuse has been used as
a source of power. After treatment it can
contribute to composts and land recovery.
65-0220
Straub, H. Amount and composition of solid
waste. In Refuse and waste disposal. Berlin,
Druckhaus Lichterfeld GmbH, 1964.
Sampling, sieving analysis, classification
analysis, sampling for laboratory tests,
determination of the moisture content,
determination of organic compounds, equipment
for mechanical analysis of refuse, preparation
of laboratory samples for analytical
examination, determination of residual moisture
content, determination of the fuel value,
self-heating tests, and determination of C/N
ratio are discussed for determining the
composition of solid waste. Instruction sheets
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0217-0227
are provided for determining the amount of
solid waste. Composition of domestic refuse
includes grain sizes, groups of substances,
water content, organic and mineral substances,
calorific value, and C/N ratio.
65-0221
Strict sanitation standards observed bv ships
at sea. Refuse Removal Journal, 8(2):6-7, 35,
Feb. 1965.
Ocean-going vessels calling at U.S. ports
from foreign countries are required to undergo
a thorough quarantine examination by
inspectors of the U.S. Public Health Service.
The examination includes a check of storage
and disposal of refuse. Continuous control
methods are necessary for the handling of
garbage and trash at sea.
The events and papers discussed at the
International Research Group on Refuse
Disposal, 3rd Congress, held at Trento, Italy,
in 1965 are summarized. The outlines of the
plants' operations are included. Papers on
landfilling, pulverization, incineration,
and composting were presented.
65-0225
Tornadoes in Midwest leave huge cleanup job.
Refuse Removal Journal, 8(6):20, June 1965.
The tornadoes that cut paths of destruction
across several midwestern states on Palm
Sunday left in their wakes an enormous
emergency cleanup operation, conducted by the
National Guard, municipal and private
contractors, and thousands of volunteer
citizens.
65-0222
Supplement to Waste Statistics 1961. Wasser
und Abwasser, 106(10) .-286, Mar. 12, 1965.
Upon request of the Federal Department of
Health, Herr Ferber, Stuttgart, worked out a
supplement to the statistics on waste disposal
for 1961. Some of the particularly interesting
results are: (1) Costs for the elimination of
wastes are highest in Hessen and lowest in
Wuerttemberg; (2) Complaints about being
bothered by waste disposal are most frequently
filed in Rheinland-Pfalz, Niedersachsen and
Baden-Wuerttemberg; and (3) A tendency
toward incineration of waste rather than
composting is observed throughout Germany.
(Text-German)
65-0223
Swiss Association for water and air protection.
Schweizerische Bauzeitung, 83(12):204, Mar. 25,
1965.
At a meeting in Olten, Switzerland, on
Apr. 9, 1965, three papers were presented:
'Water protection in the Kanton Solothurn'
by L. Looser, head of the department of water
protection of the Kanton Solothurn; 'Rubbish
disposal' by F. Keller; and 'Complete
elimination of solid and liquid waste' by
E. Wylemann. A local incinerator plant was
visited. (Text-German)
65-0224
Topics at Trento. Public Cleansing,
55(9):529-532, Sept. 1965.
65-0226
U.S. Department of Agriculture. Consumers
all--the yearbook of agriculture 1965.
Washington, U.S. Government Printing
Office, 1965. 496 p.
This hook reflects some of the facets of the
Department of Agriculture's work in behalf of
consumers and homemakers. It describes
planting, painting, wiring, heating and cooling
a house. A chapter advises proper disposal
of waste and sewage treatment. Furnishing
and interior work are discussed in the second
section. Kitchen tools, cooking, refrigeration,
dishwashers, waste disposers, incinerators,
laundry, and handy tools comprise equipment
described. Advice is given on finances:
budget, mortgage, insurance, bills, etc.
Accident prevention, health care and services
are mentioned. Help in growing plants and
landscaping is given. It describes composting
and compost usage. Various activity
suggestions are offered. Clothing selection
and care and food selection and preparation
are discussed.
65-0227
Vogel H. E. Pro Aqua Ill — international
conference in Basel. Wasser und Abwasser,
106(30):847-848, July 30, 1965.
In March 1965, an international conference
was held in Basel on 'Water and Air in
Regional Planning.' One group of papers dealt
with facilities and equipment for the
elimination of special waste which cannot be
handled by conventional rotting or incinerator
45
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Agricultural Wastes
plants. Noncombustible waste, poisonous and
certain organic material like paints and
plastics are best removed by controlled
deposition. Certain combustible wastes can
only be incinerated in special furnaces like
rotating drums. Sintering at 1,300 to 1,500 C
can convert poisonous metal containing
inorganic sludges into depositable slags
insoluble in water. A great problem is waste
from the electroplating industry. A special
centra] facility to treat these wastes was
recently built in Southern Germany. (Text-German)
A study on refuse disposal by the League of
T'omen Voters of Summit, New Jersey,
recommends that the town band together with
neighboring communities to form an authority
to operate an incinerator for refuse disposal.
An alternative for refuse disposal is the
sanitary landfill, but this method might be
disadvantageous if operated in another county.
The landfill currently used by Summit is in
the nearby town of Miele, which has scheduled
to bar outside communities from using it.
65-0228
Weston, R. F. laboratory waste disposal.
Archives of Environmental Health, 10(4):550-553,
Anr. 1965.
With the movement of laboratories to suburban
and rural areas, special problems have
been created by the limitations on waste
disposal in areas where small streams are
used for recreational or other high quality
requirements uses. Adjacent land is not
available for waste disposal , and air
pollution is not permissible. Basically, the
disposal problems are those of economically
controlling the uses of air and water in such
a manner that the quality changes involved
in its use do not interfere with the welfare,
rights, or economy of others and the vises of
the land do not destroy its economical use by
posterity. Practically every state and the
federal government have passed laws on
water pollution control. Fourteen states
have some form of specific air pollution
control legislation and 400 governmental
units have varying degrees of smoke and air
pollution control laws in their municipal
codes. The federal program in air pollution
includes appropriations to aid existing
programs and to finance new programs for local
communities. The bulk of the discussion is
limited to water pollution. Laboratory
wastewaters are a special problem, because,
although they are present in small amounts,
they can create serious pollution problems.
Nuisance water pollution can be, avoided bv
well planned in-laboratory controls, personnel
education, adequate management Interest
and well-conceived treatment facilities.
Successful disposal of laboratory wastes
cannot be carried out without substantial
cost and nuisance and must have full management
support.
65-0229
Women voters tackle town's refuse dilemma.
Refuse Removal Journal, 8(9):20-21, Sent. 1965.
AGRICULTURAL WASTES
65-0230
Agricultrual wastes. In Restoring the quality
of our environment. Report of the environmental
pollution panel, President's Science Advisorv
Committee. Washington, U.S. Government
Printing Office, Nov. 1965. p.10-11.
Farm animal excreta is a major source of water
pollution, due to surface runoff or through
seepage into waterways. Chickens are also
considered in this report. Animal manure has
been responsible for fish kills and is
considered a health hazard to humans. There
is a need for research to fine new uses and
markets for farm wastes. The generation of
manure from farm animals in comparison to
humans is shown. There is a list of findings
included.
650231
Clark, C. E. Hoe waste disposal by lagooning.
Proc. Paper 4567. Journal of the Sanitary
Engineering Division, American Society of
Civil Engineers, 91(^A6):27-41, Dec. 1965.
"Because of the poor results obtained bv the
old standard of spreading hog waste on the
land as fertilizer, lagooning was recommended,
with 10 sq ft of lagoon area per hog.
Believing lagooning to be a panacea, hog
raisers built many new installations in
Illinois. As the result of an excessively
large number of complaints, several
installations were visited in 1963, and a
sampling program was undertaken which proved
that the complaints were justified. Conditions
observed in an operation installation are
reported. The lagoons varied in size from
A sq ft to 20 sq ft per hog. The lagoons
produced a foul odor, were covered to varying
depths with scum, and large, bursting gas
bubbles were prominent. Five day BOD tests
results were extremely erratic. The large
46
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0228-0235
amounts of antibiotics included in the feed
carry over into the waste and have a marked
effect on the bacterial population of the
waste. Extremely high algal concentrations
were found in the lagoons, which led to
considerations of harvesting the algae for
use as livestock feed. It was oncluded that
the lagoon system succeeds in getting rid of
the waste with the least expense and effort.
Over the working life of the installation,
the initial cost plus the cost of operation
will amount to no more than pennies per animal
served. Provided that the lagoon is properly
located and constructed to prevent leakage to
an aquifer, ground-water polllution is not a
problem. Odors are adequately controlled,
and no pests have ever been observed, an
indication that the system is working
satisfactorily.
65-0232
Clayton, H. J. Manure produces top contest
corn yield. Compost Science, 6(1):29, Spring
1965.
Manure from 400 feeder cattle and 1,000 hogs
supplied the nutrients for the top corn yield
in Iowa's 1964 Master Corn Grower Contest.
Raymond Keppy, who produced the top yield
of 175.5 bushels of corn per acre, did not
use any commercial fertilizer, but applied
18 to 20 tons of manure per acre before
plowing. After plotting, the field was
disked and harrowed and disked again ahead of
the planter. Keppy farms 400 acres and
follows a 7 year rotation of corn, oats, and
meadow. Twenty tons of cattle and hog manure
supplies the equivalent of 100 Ib of nitrogen,
40 Ib of phosphorus, and 160 Ib of potassium.
A total of 1,330 farmers completed the 1964
contest by selecting 5 acres for a yield
determination.
65-0233
Hart, S. A., E. P. Taiganides, and H. J. Eby.
Waste disposal....pre-eminent challenge to
agricultural engineers. Agricultural
Engineering, 46(4) : 220-221 , Apr. 1965.
Highlights of a research session on
agricultural wastes management at the 1964
American Society of Agricultural Engineers'
winter of 1964 meeting in New Orleans are
reported. Urban sprawl is forcing higher
standards on agricultural sanitation.
European waste handling techniques in populous
areas will serve as helpful guides. More
research on defining and characterizing
agricultural waste is needed, as well as
positive thinking to consider manure and other
wastes as resources which can be used as fuel,
algae production, fish culturing, and in
coprophagy.
65-0234
Moorman, R. Controlling odors from cattle
feed lots and manure dehydration operations.
Journal of the Air Pollution Control
Association, 15(1):34-35, Jan. 1965.
The control of odor in the growing cattle
feeder industry is important if the operator
wishes to avoid injunctions or nuisance suits.
The growth of cattle and human population
concentrations in the same general areas
aggravates the problem. The odors in
feedlots result from poor drainage, spilled
feed, and improper disposal of carcasses,
all of hich are the result of poor planning
and/or poor management. The real odor
problems originate with the accumulation and
disposal of the manure in the feeding pens.
The necessary regular removal program may be
facilitated by black top or concrete floors.
The satisfactory methods of disposal of
the collected manure include properly
constructed compost piles, dehydration,
removal to a sparsely settled area away
from potential complainers, and spreading on
fields and plowing under. Where odor still
persists, ground and air sprays have been
tried with the preference for the ground sprays
in the feedlots. The use of manure dehydrators
is increasing as it provides a means of
extending the market to areas not available
for the green or bulk composted manures. The
dehydrator should be well-designed and have
careful control of the product flow. Odor
control becomes important to the dehydrator
operator not only during the process, but in
the storage prior to dehydrating. In
addition to the use of odor counteractant
sprays, dust collectors are required and odor
counteract ants are indicated for the finished
product. Odor control from cattle feedlots
is practical if the management is willing to
make the effort.
65-0235
Toth, S. J. Agricultural value of dried
poultry manure and bedding. Compost Science,
5(3) :29, 30, 32, Autumn-Winter 1965.
A study was conducted to determine the
agricultural value of artificially dried
poultry manure plus bedding using various
plants as test crops. Tests were run using
an automatic dryer to determine the best
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Automobile Disposal
temperature to employ without materially
reducing the N content of the final product.
The mean values for N, phosphorus pentoxide,
and potassium oxide contents of the six batches
of processed poultry manure and bedding were
3.84, 6.30, and 1.97 percent respectively.
The test field was a sandy loam soil with a
pH of 6.3. Tie test crops in 1960 were
snapbeans and sweet corn, and in 1961 Irish
potatoes. The manure and/or fertilizer was
broadcast and disced in prior to seedling.
The results which are tabulated, compare
poultry manure and 5-10-10 fertilizer, and
poultry manure and manure reinforced with
muriate of potash, the latter treatment
included because of the low K content of the
manure. Yields of snapbeans increased as the
rate of application of the manure increased
from 1 to 3 tons an acre. However, the results
obtained with 1,200 Ib of 5-10-10 were greater
than those obtained with all the manure
applications. The addition of potash failed
to increase the yield significantly. The
yields of potato tubers and their mineral
contents are tabulated. It was found that
considerable variation can be expected in the
N, phosphorous pentoxide and potassium oxide
contents of the final product, but generally
it can be considered to be a 3-6-2 fertilizer.
A ton of processed poultry manure and bedding
has about the same effect as 1,200 Ib of
5-10-10 fertilizer. The small residual value
of the processed manure and bedding was
apparent in the yield of potato tubers.
65-0236
Utilization of non-processed manure for
fertilizing fruits and vegetables.
Staedtehygiene, 16(9) : 196-197, Sept. 1965.
Three representatives in the lower house of
the federal government of West Germany
complained that no bill has yet been enacted
to control the use of non-processed manure as
fertilizers. It contaminates fruits and
vegetables with salmonella which can survive
up to 40 days after application of this manure,
and which cause numerous intestinal diseases.
A bill prohibiting the use of non-processed
manure was worked out in 1954 but could not
be enacted into law so far because of the
doubtful legality of such a bill, as State
Secretary Bargatzky Informed the complainants.
But he assured them that the government will
continue its investigations in this matter.
65-0237
Waste treatment and disposal. Farm Chemicals,
128(9):38-46, Sept. 1965.
Although there are waste treatment disposal
methods available that are versatile enough
to remove almost any harmful impurity, the
main problem is reconciling the cost of
removal with the necessity for achieving the
minimum contamination of the environment.
The basic methods of handling plant wastes are
given in an excerpt from the NAC manual on
'Waste Disposal'. The various discussions
indicate the advantages, disadvantages, and the
preliminary investigation required for each
method of waste treatment and disposal. The
methods outlined include biological, ponding,
burial, incineration, cor.tract services,
disposal at sea, chemical disposal, and
municipal treatment. A sketch is given of
waste treatment by trickling filters in which
waste after neutralization passes over
trickling filter where the film or mass of
organisms on the packing surface absorbs and
oxidizes the organic matter in the waste
water. The effluent goes to a settling basin
from whici the effluent is discharged to a
waterway and the settled solids go to a
sludge digestor, lagoon or incinerator.
Similar sketches are given of waste treatment
by activated sludge and by oxidation pond.
The use of contract services whereby some
organization removes the waste is a convenience
for industrial plants too small to warrant
in-plant disposal services, but it does not
solve the problem. Responsibility is removed
from company to the contractor, but from a
legal standpoint, there is a possibility of
both the contractor and the company being held
liable for improper handling and disposal. A
review is presented of waste treatment and
disposal methods.
AUTOMOBILE DISPOSAL
650238
Abandoned cars. Public Cleansing, 55(7):431,
July 1965.
Edinburgh's policy on abandoned cars is
described. If the owner can be located, a
2 week disposal period is set; otherwise, a
6 week impounding period during which the
vehicle can be reclaimed is established.
650239
Car disposal made easy. Public Cleansing,
55(10) :559-563, Oct. 1965.
The baling of cars in a 40-ton trailer-borne
baling press is described. This press,
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0236-0244
capable of baling two car bodies at a time,
has been hailed as the answer to the growing
social problem of abandoned cars. The
portable baler is used at the dump sites of
various municipalities in Great Britain.
65-0240
Cars drowned by Swedish skipper. Refuse
Removal Journal, 8(4):38, Apr. 1965.
Captain Otto Magnusson, skipper of the Swedish
ship, Ostkust, has a thriving business of
disposing of unwanted cars at sea. Wealthy
Sweden is producing and importing automobiles
at so fast a rate that any car over five years
old is being junked since it has no resale
value. The captain charges $22 to $32 a car,
depending on size, and the price includes
a pick up service. He loads the unwanted
jalopies on board his vessel and hauls them
to the deepest part of the Baltic Sea, where
they are shoved overboard.
65-0241
Disposal of abandoned automobiles.
Works, 96(5):82, May 1965.
Public
The disposal of abandoned automobiles is a
problem in England. Abandoned cars are not
only an eye-sore but a potential danger to
children. If abandoned in the open they should
be removed as soon as possible to prevent
accidents to children and to avoid stripping
of wheels and other useful parts; it is
costly to remove a vehicle once it has been
stripped and the scrap value may be negligible.
There may be delay in removing cars abandoned
on a street as there is no clear understanding
between police and local authorities about
their powers under the Removal of Vehicles
Regulations. It is suggested that unless it
is necessary for the police to remove the
vehicle as constituting a traffic hazard, it
should be the responsibility of local
authorities. In some cases the local authorities
themselves break up derelict cars and sell the
scrap. One authority has leased sites to car
breakers close to their depot; the breakers
strip the vehicles and sell sections to the
authority, who sell the scrap. The demand
for scrap is variable.
65-0242
English data on disposal of abandoned vehicles,
Public Works, 96(6) :92, June 1965.
Removal and disposal of abandoned vehicles is
an increasing problem in England, due in part
to the requirement for testing of vehicles
which are more than 5 years old. In Fulham,
from August to December 1963, 62 abandoned
vehicles were removed at an average cost of
about $19.00 per vehicle. Allowing an average
scrap value of $5.60, which is probably high,
the net cost is considerable. Since special
equipment is necessary for disposal, it is
recommended that depots be established which
would be financed by a group of municipalities.
These depots could be equipped with the
usual or necessary presses for baling, prior
to disposal as scrap metal.
65-0243
Hurst, S. S. Scrap motor cars--another
viewpoint. Public Cleansing, 55(11):634-636,
Nov. 1965.
Scrap metal in general is a marketable British
product, but the scrap car poses difficulties.
An outline for car breaking procedure is
given. It is pointed out that financially
it is not profitable to dispose of scrap cars
unless subsidized by the local government as
a necessary public service. Much of a scrap
yard' s revenue comes from automobile
fix-it-yourselfers. Necessary equipment for
scrapping vehicles is listed. Some countries
dump old cars unsalvaged into the ocean. Each
area must decide the method and extent of its
scrap car salvage program.
65-0244
Junked cars just don't fade away. APWA
[American Public Works Association] Reporter,
32(3):6-8, 12, Mar. 1965.
Of the 5 million automobiles taken out of
service in 1964, many were returned to steel
mills for smelting. However steel mills are
rapidly changing over to basic oxygen furnaces
which require 10 to 17 percent less scrap.
Therefore car scrap, tagged as 'least
desirable' because of its impurities of wood,
plastic, glass and metallic impurities, will
have a 16 percent loss in the market.
Statistics show that the amount and price of
scrap between 1956 to 1963 fell over 53
percent or down to $19.84 for each Number 2
bundle. Or a $3,000 car is worth only $20 as
scrap. Over half the cars junked each year
are placed in auto yards to be stripped of
usable parts. Prior to burning, the car is
placed on a 'stripping line.' The car is
then burned, cooled and pressed into a bale
2 by 2 by 4'- ft. Statistics show that in
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Automobile Disposal
1960 there were 2,500 cars abandoned on the
New York streets, and by 1964 the number rose
to 25,000. Since screening or fencing to
conceal the scrap is not sufficient, possibly
shredding or pelletizers offer some hope.
The Proler plant can process 1,000 cars per
day but the installations cost $2 million and
up, and many sections of the country can't
support the capital investment. The
Linz-Donawitz method of basic oxygen process
uses 30 percent scrap while the Stora-Kaldo
uses 55 percent. This rate of consumption
offers some hope for the future. However we
cannot sell more scrap than the steel mills
can use.
650245
Lloyd, G., and R. McCann. Waging war on
abandoned autos. American City, 80(11):98-100,
Nov. 1965.
The number of abandoned autos has increased,
and the Chicago Police Department has found
it increasingly difficult to perform its duties
including towing. Some of the restricting
circumstances are the almost complete absence
of tow trucks, inadequate organizational
structure and procedures, legal restrictions
on the method of disposal as stated in the
State law, and inadequate facilities for
storing abandoned autos. To meet the ciisis,
private towing concerns were contracted and
towing immediately surged. The organization
and procedures dealing with abandoned autos
were changed. Formerly, the responsibility
rested with the Stolen Auto Section of the
Detective Bureau, but the Auto Pounds Section
was created to have complete control over
towing, custody, and disposal of impounded
autos. In September 1960, the department
operated eight pounds for the storage and
safekeeping of cars, but since that time the
number of pounds were reduced and the
specialization of functions eliminated. An
amendment to the State law granted permission
to sell the autos by competitive bidding to
junk dealers. This resulted in a more rapid
turnover in available storage space. The
removal and custody of abandoned autos only
occurs with those which are in a complete state
of disrepair (no engine or wheels), or those
which have not been moved for 7 consecutive
days. Vehicles of 1960 vintage or newer,
automatically receive an appraisal of $100
or more, therefore going to the auction block.
Contract terms call for sales to licensed
automobile wreckers or used-parts dealers
only.
65-0246
New York to accept unwanted jalopies. Refuse
Removal Journal, 8(4):28, Apr. 1965.
In order to do away with the abandonment of
old cars on city streets, the Department of
Sanitation of the City of New York is offering
the facilities of its encumbrance yards,
garages, landfill, and incinerators to motorist;
who wish to dispose of unwanted vehicles
legally. The action was taken in anticipation
of a large number of motor vehicles which
owners probably will relinquish rather than
incur the expense of new registrap;ions,
insurance renewals, and other costs. The
Department sites will be available throughout
1965. Owners may drive their vehicles, or have
them towed to any Department base in their
home vicinity. The city prefers private means
of legal disposal, including selling old cars
to junk dealers, but would rather accept them
at all Department locations, than have the
autos abandoned to become street hazards.
650247
Operation clean sweep. Western City, 41(3):27,
Mar. 1965.
Merced (population 23,000) initiated a new
program whereby the city removed substandard
housing. This program later inspired
'Operation Clean Sweep'. The Department of
Motor Vehicles together with police and Fire
Prevention Bureau located abandoned cars on
private property and removed them at no
charge. In the first few months 165 vehicles
were removed and approximately 50 more were
waiting. This program has given the city a
new look and has spurred additional capital
investments to further protect assessed
valuations.
65-0248
Pelletizing scrap. Waste Trade World,
106(25):3, June 19, 1965.
The car disposal problem was the center of
attention at the SIR congress. A color film
was shown on the Luria 'auto-eater' fragmentizer
(or pelletizer) technique. Mr. Luria was
present to answer questions after the showing.
The film showed the giant plant, which is
installed in Los Angeles, together-with
close-ups of car bodies entering the 'mouth'
of the machine and coming out at the other
end in the form of pellets which can be varied
in size for specific purposes. The main
technical advantages are a cleaner end-product,
scrap in a form more suitable for new
50
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0245-0253
steelmaking techniques, and the elimination
of incineration. Economically, the fragmentizer
t echnique is not easy to fit into European
conditions, although a smaller model for less
concentrated scrap areas is now being developed.
65-0249
Portable crusher speeds auto salvage. Refuse
Removal Journal, 8(9):32-33, Sept. 1965.
An auto bodv crusher, made by Aljon, Inc.,
compresses an average body into a 6-in. thick
slab in about 5 minutes. The unit used by
the Alter Co. of Davenport, Iowa, can be
transported in a flat truck from one salvage
yard to another. Scrapped cars are pulled
through the machine by an endless cable
arrangement.
65-0250
Shults, F. Getting to grips with the problem
of littering cars. Public Cleansing,
55(2) :110-1 14, Feb. 1965.
The formation and operating procedures of an
abandoned vehicle department in the London
fringe area of Tottenham are reported. Safety
inspections have increased the number of
abandoned vehicles into a traffic and safety
problem. A reportedly abandoned vehicle is
first inquired about and inspected. This
effected the removal of about one-half of
the 239 vehicles reported in the 8 months the
department has operated. The city contracts
for $5 per car for towing of abandoned cars
to an impounding area, where they are kept for
2 months, and then sold to the high bidders
to recover costs. Copies of the abandoned
vehicle report, and report for disposal of
vehicles brought in by owners, and analysis of
the department's results are included.
65-0251
Shults, F. London centre discusses abandoned
vehicles. Public Cleansing, 55(12):698-709,
Dec. 1965.
A paper and discussion on Britain's abandoned
vehicle problem is presented. Elimination of
the long administrative procedures necessary
to deal with abandoned vehicles and a specialist
to head an area's vehicle disposal and develop
a liaison with police are considered. A
brief outline of the city of Tottenham's
abandoned vehicle program is included where
cars are impounded for six weeks and then
auctioned to scrap dealers. There is a trend
towards plastic car bodies which may complicate
disposal in the future. It is suggested that
emphasis be shifted from local authorities
finding owners to having owners seek out their
car after it is impounded. A list of British
legislation on abandoned vehicles is included.
The discussion brings out that 85 percent of
old cars are dealt with by scrap merchants
and industry, who were also willing to pay to
dispose of the municipal's 15 percent. Police
coordination is emphasized, and contract
methods of disposal operating in several
British communities are explained.
65-0252
Solid wastes. Automobile hulks. In Restoring
the quality of our environment. Report of the
Environmental Pollution Panel, President's
Science Advisory Committee. Washington, U.S.
Government Printing Office. Nov. 1965.
p.154-156.
The current junk car problem is generally
conceded to be 'visual pollution'; its genesis
is primarily economic rather than technological.
Old automobile hulks represent a source of
important scrap metal, however; the objective
is and should continue to be their reconversion
to industrial use. A number of influences are
acting to interrupt a normal recycling of
scrap from old cars back into steel furnaces.
The cost of collecting, processing, and
transporting auto hulks is high and the price
of the product is low compared to other
desired forms of ferrous metal scrap; changes
in the steel-making process require less scrap
than formerly; and the number of autos junked
each year is steadily increasing. Some
research is in progress to find uses for auto
hulks other than as scrap steel. The most
promising seems to be combining the scrap with
low grade taconic ore in order to make it
magnetic and improve its characteristics.
Other possibilities include: (a) to design
automobiles so they can be more easily
cannibalized; (b) to increase the interchangeability
of auto parts, so that the junk car might be
cannibalized more rapidly for its parts; and
(c) the consider the reconcentration of auto
hulks, in effect building an artifical iron
mountain as a future resource.
65-0253
Soraerville, A. T. The problem of abandoned
cars and vehicles. Public Cleansing,
55(10) :596-599, Oct. 1965.
The general abandoned car problem is
considered. The introduction of the compulsory
51
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Automobile Disposal
vehicle test has magnified the abandoned car
problem in London to 6,000 in 1963.
Manchester offers 4 centers for free disposal
of old cars; Tottenham removes cars to a
pound after an attempt to notify the owners,
South Shields posts a notice on the car,
photographs it, and then 6 weeks later removes
the car. A city undertaking car disposal
needs a break-down vehicle with a crane, or
lifting arms to remove old cars, oxyacetylene
cutter, and a baling press. Hiring of a mobile
baler requires at least 200 car bodies to be
economical. Difficulties in storing and
cleaning scrap car bodies, metal and fiber-glass,
are mentioned.
year. An appendix listing British laws
enabling cities to dispose of vehicles is
included. The committee agreed that it was
the loca] authority's responsibility to
offer a free collection and disposal service
for unwanted vehicles, that vehicles should
be incinerated to obviate smoke and smell,
and that a mechanical baler for sheet metal
parts be provided. Findings of a committee
of city engineers in the 500,000 Hemel
Hempstead, England, area on a scheme to
dispose of abandoned and derelict cars are
reported. The scheme as proposed involved
a consortium of local councils, and finance
was to be apportioned on rateable value. The
study involves data on estimating number of
vehicles.
65-0254
Story, W. S. Need measures to aid abandoned
car salvage. Refuse Removal Journal, 8(11):20,
Nov. 1965.
The scrap industry is an important part of
national conservation of resources, for it
can be used in place of iron ore, coke, and
limestone in making new steel. Five million
tons of scrap were provided in 1964 by junked
cars alone. The scrap industry has special
equipment for handling auto scrap, to shred,
refine and mill the scrap. What is needed,
more than anything else is a ready market for
scrap. Car abandonment problems are discussed.
It is suggested that the time limit to claim
cars be shortened, and that licenses be
required for private citizens having more
than two or three abandoned cars on their
property.
65-0255
Turner, A. H., A. S. Moody, and H. Wilkinson.
Collection and disposal of abandoned and
derelict cars. Public Cleansing, 55(9) :536-544,
Sept. 1965.
Findings of a committee of city engineers in
the 500.000 Hemel Hempstead, England, area
on a scheme to dispose of abandoned and
derelict cars are reported. The scheme as
proposed involved a consortium of local
councils, and finance was to be apportioned
on rateable value. The study involves data
on estimating dumber of vehicles which would
require disposal, the facilities and location
of the central depot, vehicle delivery and
storage, salvage technique, labor requirements,
and cost estimates. The committee estimated
that equipment and land suitable for 8 to 25
cars per day could be purchased at $250,000,
and that the total excess of expenditure over
income from salvage would be about $43,000 per
65-0256
U.S. scrap car study. Waste Trade World,
107(26):9, Dec. 25, 1965.
The U.S. Bureau of Mines is conducting a
nationwide study to obtain a definitive
picture of the scrap car problem and the
complex factors underlying it in different
parts of the country. Detailed interviews
with selected auto wreckers and scrap processors
will focus on where and why scrap cars are
piling up. The study is designed to provide
data for two major Government objectives: the
conservation of valuable metals contained in
scr'ap cars and the removal of the
"auto-graveyard" which spoils the natural
beauty of the landscape. The Bureau feels
that the causes for instability in the scrap
metal market, which need to be defined and
removed, vary from one part of the country
to another. Data obtained from the study
will be used to plan regional conservation
and beautification programs.
65-0257
Vehicle disposal in a standard press. Public
Cleansing, 55(4):202-203, Apr. 1965.
A 100 ton metal baling press in Sal ford,
England, used for disposing of tin cans, bikes,
and other scrap metal, has been used for
vehicle baling. The vehicle is systematically
cut up by oxy-acetylene burners, then further
cut by the press, and finally contained
within the press and baled. A large, burned
out car was reduced to 8 bales totaling 1,300
Ib and about 1 ,400 Ib of other metal from
axles, engines, etc. Two men could bale 6
cars in 8 hr using the press.
52
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0254-0261
COMPOSTING
65-0258
Another plea for research. Public
Cleansing, 55(6) -.352-353, June 1965.
Composting of refuse to replace valuable
constituents in soil which are removed by
cultivation is reported. The Dutch use
this system, but decreasingly because of
increasing contraries in compost. Research
to establish the real value of compost,
the effect of contraries, and the
biochemistry involved is recommended.
65-0259
Beckett, J. L., and H. R. Oakley. Sewage
disposal and refuse composting in Leicester,
England. Compost Science, 6(1):5-8, Spring
1965.
An integrated system for the treatment
and disposal of sewage sludge and refuse
in the City of Leicester, England, is
described. A sewage treatment plant and a
refuse composting plant were built
adjacent to each other and their activities
coordinated. The Dane Bio Stabilizer
process was used in the composting plant,
and six stabilizers, providing a total
capacity of 325 ton per day, were
installed. Equipment for salvage was
also provided. For the sludge drying
in the sewage plant, four Komline coil
filters were selected. These were
arranged so that the outer two filters
each feed a single Bio-Stabilizer and
the two inner filters each discharged to
two stabilizers. The whole plant was
designed on the basis that the minimum
quantity of sludge will be dried and the
maximum quantity of sludge fed wet to the
stabilizers. Operation of the plant will
be controlled so that wet sludge is added
to each unit to ensure that the
combined moisture content of the mixed
refuse, dried sludge and wet sludge, is
between 50 and 60 percent. The design
and operation of the composting plant,
which in addition to the Bio-Stabilizers
includes an incinerator, and provision
for salvage, is described in detail.
Total cost of the plant is estimated at
£3,720,000. Detailed specifications are
given for the reception hall, salvage
hall, Dano Bio-Stabilizers, and screening
houses.
65-0260
Behe, R. A. Disposal of municipal
garbage by composting. Journal of
Environmental Health, 27(5):82A-829 , Mar. -
Apr. 1965.
Composting of garbage has attracted
considerable interest in the United
States during the past several years.
It has been practiced in Europe and
Israel for many years. Sanitary landfill
disposal is a necessary part of the
composting system for disposal of
non-compostables and non-salvageable
items. This material represents only a
small percentage of the total refuse. In
Altoona, Pennsylvania, one of the
successful composting plants in the
United States is located. It has been
in operation for 31- years. The present
daily input of refuse is 35 to 45 tons.
Garbage is deposited on a platform
outside and is pushed into two grinders
by a front end loader. A 40 hp, 650 rpm
motor operates the grinders. Tungsten
carbide tips shred the material into a
finely ground slurry, and the ground garbage
is discharged into a collection tank. A
screen in the tank separates the scrap
trash. The garbage is forced into the
dewatering screws and then transported
to trie windrows by truck. A digester,
recently installed, has replaced the
windrowing. This digestor has many
outstanding features, among which is
lack of objectionable odors. The compost
is still put in windrows for a short
curing time. It takes only 4 or 5 days
to reach this point. Then, the compost
is fed into a dryer for about 20 minutes
and finally is ready for shipment. This
operation is fully automatic and
involves little manpower. There are no
public health problems connected with the
operation. It is flexible in that it can be
applied to any composting operation and
can be used for digestion of garbage as
well as sewage sludge.
65-0261
Bell, C. W. Put your leaves to work.
American City, 80(8):112-113, Aug. 1965.
The efforts of Neosho, Missouri, a
city of 7,750 people, in preparing compost
from the fall leaf collection for use in
3,340 flower plots and boxes in the city
are described. Cost of the project is
$2,618. Manures, sawdust, wood chips,
phosphate, and limestone are added to
enrich the compost and speed the composting
process to completion in about 2 weeks.
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Composting
65-0262
Blonk, D. M. de. Engineering behavior of
a waste conversion end product. Defense
Documentation Center. [Pittsburgh, Pa.],
University of Pittsburgh, 1965. 111 p.
(NTISrAD 617290.)
A look at the engineering behavior of the
end product of a waste conversion process
used as a landfill is presented. The
laboratory program investigated the
densities of the compost material and
subjected it to the compression, compaction,
consolidation and the California bearing
ratio tests used in engineering practices.
The behavior of the compost as a result
of the above tests is tabulated. A
general discussion of the laboratory
results is given. The engineering
behavior of compost used as landfill
based on supporting data is examined.
Advantages, disadvantages, applicability
and related problems are defined.
Recommendations for future study,
appendices, a bibliography, and list of
uncited references are included.
65-0263
Blonk, D. M. de. Laboratory program.
In Engineering behavior of a waste
conversion end product. (NTIS:AD617290)
Defense Documentation Center. [Pittsburgh,
Pa.], University of Pittsburgh, 1965.
p.4-9.
The waste conversion end product material
(compost) used in this investigation,
as received, had a moisture content of
from 49 percent to 58 percent of dry
weight (at 105 C). The specific gravity
of a soil is often used in relating
the weight and volume of a soil. Unit
weights are needed in nearly all measures
of pressure settlement and slope stability
in soil engineering. Thirty-two compaction
tests were used to determine compaction
behavior and were conducted with moisture
contents varying from 12 percent to 98
percent. Tests used were: the Harvard
miniature compaction test; the standard
Proctor compaction test; the static
compaction test; unconfined compression
test; triaxial compression test;
consolidation test; and California
bearing ratio test. The total weight,
moisture content, and dry density were
determined in each test sample.
65-0264
Blonk, 0. H. de. Results of the test
program. In Engineering behavior of a
waste conversion end product. Defense
Documentation Center. [Pittsburgh, Pa.],
University of Pittsburgh, 1965. p.10-14.
(NTIS:AD 617290.)
The specific gravity of the solid portion
of the sample material used, as determined
by standard soil methods, was 2.1. Results
of the compaction and compression tests
are shown in appendices. For the Harvard
Miniature compaction tests, the optimum
moisture content ranged from 58 percent
to 62 percent of dry weight at 105 C.
The maximum dry density obtained was
50.8 Ib per cu ft at a moisture content
of 60.9 percent. The optimum moisture
content for the Standard Proctor
compaction tests ranged from 65 percent
to 72 percent of dry weight at 105 C,
and the maximum dry density obtained was
45.4 Ib per cu ft at a moisture content
of 67.8 percent. The static compaction
tests gave an optimum moisture range of
20 percent to 24 percent of dry weight
at 105 C with the maximum dry density
obtained of 59.7 Ib per cu ft at a
moisture content of 22 percent. The
stress controlled samples showed a
greater unconfined compressive strength than
the strain controlled tests; however,
the results from both series of tests
were similar. Unconfined strength seems
to be independent of water content or
dry density in the range of optimum
moisture. The appearance of the stress
vs. strain curves for confined compression
behavior tests were similar to those of
the unconfined test except that the former
had larger values of stress resulting from
the confining pressure. The test
results of the California Bearing Ratio
indicated that the CBR value is
dependent on the dry density at a
constant moisture content.
65-0265
Blonk, D. M. de. Discussion of laboratory
results. In Engineering behavior of a
waste conversion end product. Defense
Documentation Center. [Pittsburgh, Pa.],
University of Pittsburgh, 1965. p.15-19.
(NTIS:AD 617290.)
The behavior patterns of ordinary engineering
soils are not clearly understood. Soil
systems consist of three phases: inorganic,
solid mineral grains; water, either
absorbed on the surfaces of the grains or
free in the void spaces; and air (or
other gases) existing as discontinous
air space through the soil system. The
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0262-0268
behavior of the compost material is
additionally complex, due to its
composition and the related biological
and chemical action. The total densities
of the laboratory samples were from 55
to 82 lb per cu ft as compared to a
previous field test sample yielding
12.8 lb per cu ft. It is thus apparent
that a waste conversion end product,
compacted to a dry density of 50 lb
per cu ft, would give a greater reduction
in volume of refuse material. Compression
behavior data shows that the waste conversion
end product is much more compressive than
ordinary fill material or the soil upon
which structures are usually found.
65-0266
Blonk, D. M. de. Engineering behavior
of compost landfill. In Engineering
behavior of a waste conversion end
product. Defense Documentation Center.
^Pittsburgh, Pa.], University of
Pittsburgh, 1965. p.20-41. (NTIS:AD
617290.)
Availability and light weight are the
advantages of using compost material in
land reclamation. Evaluation parameters
used in this hypothetical case are:
total height of the finished landfill is
20 ft; the material is placed in layers
at the rate of 3 ft per month; the material
has the same properties as determined by
previous laboratory tests; and the
underlying soil presents a good
foundation. Using the above parameters
the following aspects were considered:
method of placement; trafficability of
the fill at all stages; settlement of the
surface of the fill versus time; bearing
capacity, settlement, and foundation
treatment for structures on the completed
fill; pavements used for highways or
airfield runways; general considerations
for supporting utilities and slopes
terminating at the fill area. Supporting
data are given in equations, tables,
and charts.
65-0267
Blonk, D. M. de. Summary and conclusions.
In Engineering behavior of a waste
conversion end product. Defense
Documentation Center. fPittsburgh, Pa.],
University of Pittsburgh, 1965. p.42-44.
(NTIS:617 290.)
In using standard soil mechanics
techniques to evaluate the behavior of
the compost material in engineering
situations the following conclusions are
drawn: the compost product can be
successfully utilized as a fill material;
while not the best landfill material,
its advantages are availability and
light weight; filling should be carefully
controlled and continual checks should
be made of the dry densities of the 8-in.
compacted layers; landfills should be
capped with a suitable covering; slopes
terminating at the landfills will be
stable at 1^ horizontal on 1 vertical
if properly protected; the surface of a
completed landfill will ultimately settle
from 3 percent to 8 percent of the total
thickness due to its compressibility;
foundation types are limited to secondary
structures using spread footing, one story
and light 2 story buildings on raft
foundations, larger buildings on caissons
through the fill; use of roadways and
runways should be limited; and as the fill
is being constructed it will probably be
trafficable to all but the heaviest
trucks and construction equipment.
65-0268
Blonk, D. M. de. Recommendations for
future study. In Engineering behavior
of a waste conversion end product.
Defense Documentation Center. [Pittsburgh,
Pa.], University of Pittsburgh, 1965.
p.45-47. (NTIS:AD 617 290.)
Laboratory studies and field tests are
recommended for future study of composts
used as landfills. The laboratory studies
might include: chemical analysis to
investigate the nature, magnitude, and
rate of the biological and chemical
processes; investigation of engineering
behavior with avriations in composition
of the compost material; the effect of
chemical or biological degradation of
the material upon its engineering
behavior; and investigation of the
hydraulic behavior (permeability) of
the material. The field tests might be
done on a large scale field situation
with the construction of a landfill of
compost material 20 ft high and the limited
width. Field measurements of the material
might involve: moisture content; density
measurements; settlement studies versus
time; load carrying capacity; negative
skin friction; and uniformity of
temperature throughout the fill. For a
more thorough analysis smaller fills
should also be constructed.
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Composting
65-0269
Bridger, R. The ABC of waste conversion
- Part I. Compost Science, 6(1):27-29,
Spring 1965.
With the world population increasing about
50 million annually, substantial amounts
of farm crops and domestic livestock will
be needed in the future. On a world
average, it takes about 1-? acres of
cultivated land to support each person,
and the soil bacteria which may be derived
from waste products are of great
significance in maintaining our ecosystem.
Animal manure may not always be incorporated
directly with the soil, but may first
interact with vegetable residues on the
surface, in which case sheet composting
will occur. Plant debris, which has
accumulated from the previous season's
growth, is slow to disintegrate of its
own accord. It has been shown that the
organisms decomposing the celluloses
and pentosans require a definite amount
of nitrogen. Nitrogen is a very unstable
substance and added in isolation can make
little headway. For an increase of one
part of nitrogen in the soil, ten parts of
carbon must be added. If farmyard manure
is used properly, fermentation will take
place and the result will be a comptost,
The least losses in storing farmyard
manure occur when the manure is carted
direct to the fields from the animal
sheds or stored under anaerobic conditions
at a temperature of 26 C. Farmers are
decreasing in number and livestock wastes
are not being regarded as something to be
made the most of, but looked on as just: a
nuisance.
65-0270
Brunt, L. P. Composting treatment of
town refuse and sewage sludge. Institution
of Public Health Engineers Journal,
64(2) :73-99, Apr. 1965.
This review of the technological aspects
of the composting process and its
application to the treatment of refuse
and sludge also reviews the other
established methods of treatment for
purposes of comparison. Limitations with
special attention to controlled dumping,
pulverizing, and incineration are
discussed. Four tables are given of
the data covered in the discussion.
Table 1 covers the characteristics of
refuse in Great Britain showing the
percentages of the various components
which in the estimated overall anal/sis
for 1964 show 25 percent paper and
cardboard, 10.5 percent vegetable and
putrescible matter with an average of
325 Ib per cu yd. Table 2 shows the
results of pulverizing of the refuse
while Table 3 gives the data on composting
treatment of the refuse, and finally the
data on incineration of refuse is given
in Table 4. It was concluded that
there was a possibility that many towns
in Great Britain may be able to dispose
of a significant quantity of the sludge from
their sewage treatment works by composting
with the available garbage from their
refuse. The content of animal residue
in the garbage itself, such as meat and
fish scraps, food wastes, dung from
sweepings, dead birds, dogs, and cats
fell short of the level required for
true composting and thus sludge treatment
is required.
650271
Bylin, J. E. More cities discover savings
in converting garbage to fertilizer. The
Wall Street Journal, 166(38):1, Aug. 24,
1965.
In order to trim garbage disposal costs,
Elmira, New York, has its rubbish converted
to compost, a soil conditioning material,
which itself enriches the soil, or when
chemically treated, produces fertilizer.
Elmira will save $30,000 (costs now are
$117,000 per year) in disposing of its
20,000 tons of trash. Houston, St.
Petersburg, Rochester, and many European
cities have adopted similar programs.
National Organic Corporation, Westinghouse,
Allstate Insurance, and Foster Wheeler
Corporation represent companies making
commercisl use of refuse, an increasingly
popular plan due to lack of available burial
sites. Presently, 150 million tons per
year of trash is thrown away; by 1980,
260 million tons will be generated. The
Federal Government is presently attacking
the problem with studies and grants. At
Elmira, NORCO breaks down all rubbish
for soil conditioner, unlike other
companies which salvage tin and glass
(25% of trash) for sale. Formerly slow
compost sales hampered private ventures,
but now cities subsidize part of expenses.
Other proposed ways to use rubbish for
profit include transferring it into gas
and charcoal (Pan American Resources, Inc.),
power for desalinization plants
(Foster-Wheeler), and electrical generator
power (TRV).
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0269-0275
65-0272
Composting.
July 1965.
American City, 80(6):13,
Nine members of the House have introduced
bills on new refuse disposal methods,
authorizing $7,500,000 for demonstration
plants and $7,000,000 per year for
provisions of the act.
65-0273
Composting gets a tryout. American City,
80(4): 99-102, Apr. 1965.
SACS, Inc. operates a composting plant
in San Fernando, California, which costs
$9,000 to $14,000 per ton to build and
$3.50 to $4.50 per ton to operate. The
final product is less than 20 percent of
volume and about 80 percent of weight of
incoming refuse. Metal, lumber, paper
to be shredded, rags, rubber, plastic and
glass are salvaged--representing about
20 percent of refuse handled. Remaining
material enters a pulverator. The
tumbling action mixes water with refuse
to a moisture content of 45 to 65
percent where decomposition takes place
best. An impact-type grinder, with flails
fastened to a rotating shaft by chains,
further reduces size. The material is
aerated in the digester. Temperatures
averaging 160 F kill harmful organisms
and weed seeds. After composting, the
material passes into a rotating screen to
separate fine material from the coarse. The
final product has one percentage nitrogen,
one percentage phosphorous, and one percent
potash. It is similar to peat moss. It
complements fertilizer, but is not a
substitute. For plants processing 150
to 300 tons per day, the developers
recommended 3'< acres. San Fernando
disposes of refuse at SACS at a cheaper
rate than by haul to a landfill in the
foothills. The process does not contribute
to air pollution.
65-0274
Davies, A. G. Points to consider in
refuse disposal. Compost Science, 5(3) : 23,
Autumn-Winter 1965.
The amount of refuse to be disposed of
annually will increase in volume
disproportionately to weight, whatever
system of disposal is adopted--controlled
tipping, incineration or composting--a
large proportion of the refuse must go
back into or onto the land, and the land
available for untreated refuse is limited.
The English towns of Cheadle and Gatley
have chosen the Simon-Lawden compost
process. The plant is designed to deal
with 57 tons of household refuse per day,
but may be extended. Crude refuse is
received at a low level hopper. The
refuse is then conveyed beneath a magnetic
separator, and salvageable material is
hand-picked from the same belt. The
tailings are roughly pulverized and
conveyed by bucket elevator to a digester
where the decomposition of refuse takes
place. The plant will require one
foremen, one tractor driver and six
laborers for its operation. A range
of twelve standard-unit plants is
designed to cover all normal requirements
for communities varying in population
from below 50,000 to over 300,000. The
range consists of three basic types of
plant, for transfer, incineration and
composting respectively, each available
in four sizes. The composting plants are
designed to process household refuse
from which all the tin, and a certain
amount of paper, has been removed. The
process consists of retaining the refuse
for 5 days within the digesters through
which the refuse moves slowly at a
controlled rate.
65-0275
Donhue, J. R. The development of compost
plant design. Public Cleansine,
55(4):209-217, Apr. 1965.
A history of compost plant development
with descriptions of the operation of
plants following the windrow, vertical,
and Fermascreen systems, with arguments
favoring the Fermascreen system for
cities of less than 50,000 is reported.
General discussion of pulverization,
sorting, mixing, fermenting, glass
separation, and economy are included.
Large compost plants, illustrated by the
Bangkok 325 ton per day plant, require
several different machines and operations
to prepare the refuse. The Fermascreen
method, involving a single wire barrel
which can be rotated, allows pulverizing,
mixing, and alternate decomposition and
agitation, and finally sorting of the
conglomerate into usable compost, and
glass, rags and other wastes, all in one
machine. The Fermascreen type of
machine is especially efficient for small
scale composting operations. (Text-German)
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Composting
65-0276
Dyal, R. S., and R. R. Robinson. Organic
matter. In Consumers all — the yearbook
of agriculture 1965. Washington, U.S.
Government Printing Office, 1965.
p.221-224.
Improving soil condition with organic
matter increases plant growth and root
development. Leaves, manure, and plant
wastes containing nitrogen are often used.
Never put meat scraps in a compost pile.
Soft organic materials, such as grass,
compost better when mixed with coarse
material. Smaller particles decompose
faster than larger ones. The pile
should be moist and large enough to
maintain favorable temperatures. Optimum
size is 6 ft high and 5 to 6 ft wide with
alternate 6'in. thick layers of organic
material and soil. One cup ammonium
sulfate, one-half cup superphosphate, a
tablespoon of epsom salt, and two-thirds
cup ground limestone per packed bushel
should be added as nutrients. A flat top
that slants toward the center catches
rainfall. Composting wil] not kill all
disease-carrying organisms and weed seeds.
Procedure for spreading fertilizer and
organic matter on various types of plants
is given.
65-0277
English, M. C. The economics of composting
in Holland. Public Cleansing, 55(3): 146-148,
Mar. 1965.
The costs, agencies, and markets oE
compost in Holland are reported. V.A.M.
(Dutch for Refuse Disposal Company, Ltd.)
manufactures 50 percent and distributes
75 percent of all the nations 210,000
ton per year compost output. An increase
in quality of the compost, eliminating
glass and clinker, has opened markets to
vegetable, fruit and bulb growers and
also on lawns and parks. Buyers pay $1.70
to $4.50 per ton, depending on quality,
plus shipping costs (about 50% of compost
price.) The company's loss on production
and sale, presently $1.55 per ton is
made up by the cities disposing of their
refuse through V.A.M. About 25 percent
of Holland's municipal refuse is disposed
of by composting, primarily through the
government-instituted agency of V.A.M.
Municipal costs of $4 to $5 per ton for
total collection and disposal are common.
Without V.A.M.'s national initiative,
composting would probably not be feasible.
65-0278
Farkasdi, G. Do additives affect windrow
composting of refuse and sludge? Compost
Science, 6(1):11-13, Spring 1965.
The effect of various additives on windrow
composting of refuse and sludge is
presented. In experiments conducted in
1961 and 1962 at Giesen University Institute,
three accelerating agents 'Edafil' , 'Proteg
Oleo', and 'Zusaetze-Frankfurt', and two
compost starters 'Multibacto' and 'B.D.
Starter' were tested. The effect of
these additives was checked by composting
without grinding (Baden-Baden system),
by composting with grinding (Rasoing
method) , and by windrow composting
following pre-composting in a digester
(Dano process). The experimental windrows
were 1.5 m high, 2.0 m wide, and 5.0
m long. Two parallel windrows were
treated with the same additive, the
piles were stacked in layers and the
additives were suspended in water and
appropriate amounts were evenly mixed
into the piles. The control piles received
an equivalent amount of chlorine-free
water and specially prepared samples of
refuse put in porous plastic bags and
placed in the middle of the piles.
These samples, for subsequent examination,
were separated as to pathogenic and
non-pathogenic content. Piles were
turned during the third, sixth, and ninth
weeks, and were dismantled after about
14 weeks of composting. Samples were
taken for examination after each turning
and after completion. The physical tests
were for temperature, reaction (pH) , and
particle size, and the chemical tests for
carbon dioxide, oxygen, water, and ash
contents, as well as volatile solids
and ammonia content. The microbiological
tests included the determination of total
germ counts and self-heating capacity.
Tabulated results are presented for
speed of temperature rise on the seventh
day, rise of temperature above 55 C
and variations in ammonia content. It
was concluded that the results of many
experiments indicated that no significant
effects were obtained with the
stimulating or inoculation agents that were
used. The use of additives did not
show any hygienic advantage.
65-0279
Fuller, W. H., and S. Bosma. The
nitrogen requirment of some municipal
composts. Compost Science, 6(2):26-32,
Summer 1965.
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0276-0282
Any reduction in time necessary to
prepare a mature compost greatly
enhances the chance for a successful
operation. The time necessary for
decomposition processes to produce a
mature compost is dependent upon such
chemical factors as: the relative
proportion of the major plant constituents
present, such as cellulose, hemicellulose,
polysaccharides, etc., and the relative
proportion or ratio of nitrogen to
carbon. In general, materials of C/N
ratios above 40 require nitrogen in
order to attain maximum rates of
decomposition. The simplest and most
accurate method for evaluating the
need for nitrogen is to add small
increasing increments of nitrogen to the
compost and measure the effect on the
general biological activity as indicated
by intensity of respiration. Composting
procedures do not suggest the addition
of nitrogen, for the most part. The
initial C/N ratio of municipal refuse
in the United States varies from about
30 to 80 with most above 50, the addition
of some nitrogen-containing material is
advantageous. As decomposition progresses,
C/N ratios narrow. Raw commercial garbage
generally has 1.2 to 2.7 percent nitrogen,
although this figure is less for U.S.
municipal garbage. When ammonium sulfate
was increased to a rate of 2.0 percent
of partially digested municipal refuse, a
significant decrease in mlcrobial activity
and composting was found. The effect of
ammonium sulfate and ammonium hydroxide on
the rate of biological attack on mature
compost both alone and mixed in a soil
were studied. When applied to the soil
they had a slightly more inhibitory effect
on microbial activity than when applied
to the compost alone. Inhibition of
microbial activity by ammonium sulfate
and calcium nitrate is due to the high
salt effect on osmotic tension of the
solution, however inhibition by ammonium
hydroxideappears to be due more to a
direct toxic effect of the ammonia
molecule than to a salt effect.
65-0280
Garbage composting. Journal of the Water
Pollution Control Federation, 37(5):644-646 ,
May 1965.
An international review of composting
is presented in the form of brief
statements covering 31 articles. All
organic wastes may be combined in the future
to produce a consolidated, stabilized
end product useful as a raw material;
the United States is 10 years behind in
appreciating the problem of environmental
health and especially that of solid waste
disposal. The principal elements of
composting are listed as presorting,
screening, shredding, screening,
pulverizing, composting, and maturation;
composting is called competitive with
incineration in both capital and operating
costs. New equipment and processes
are continuing to be developed for
composting garbage; Rome is using the
Gianotti system for one of its four
composting plants which includes a 70
metric tons per day plant for material
which cannot be composted. Before the
plants were in operation, the city of
Rome used 400 trucks to deliver refuse to
local farmers who spread the refuse over
the land or composted it first; Caspari
has developed a process for combining
household refuse and sewage sludge to form
a stable end-product at Schweinfurt,
Germany. The Kingston, Jamaica composting
plant, which processes about half of the
city's 120,000 tons of refuse per year,
uses a grinding and windrowing method;
experiments in Indonesia indicate that
in small tropical cities the wastes can
be composted in an economical and sanitary
manner by simple windrowing. A bibliography
is included.
65-0281
Keegan, P. Tenafly, New Jersey, welcomes
city leaves. Compost Science, 5(3).'16-17,
Autumn-Winter 1965.
Each November in Tenafly, New Jersey,
a huge compost pile is made out of the
17,000 cu yd of leaves collected. The
program began over 10 years ago. The
finished compost is used in public parks.
This is a great saving for the town,
for if the composted leaves were not
available, topsoil would have to be
purchased. Tenafly has an ordinance
against burning leaves and air pollution,
and the residentr, cooperate with the
local government by placing the leaves
on roadsides for the vaccum pickup
machine. Since the pickup of leaves
became standard throughout the community,
catchbasins and drainage systems need to
be cleaned only one-third as often.
65-0282
Leatherhead - sewage treatment and
composting. Water and Waste Treatment,
'10(7).-362, May-June 1965.
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Composting
A detailed report on the Leatherhead
Sewage Treatment Plant and the
new composting plant, presented by the
plant manager at a meeting of the
Institute of Sewage Purification (Apr.
8, 1965), is summarized. The new composting
plant, the first mechanized one in England,
was installed to replace an older one
which composted refuse and sewage by an
open bay method. Installation costs were
674,00 for a population of 45,000.
Composting is carried out in a Dano
bio-stabilizer, 74 ft long by 9 ft 1 in.
in diameter, which holds up to 80 tons of
refuse. The stabilizer is rotated by a
45 hp motor at about 1 rpm during the
working day. Refuse tailings are fed
into the non-rotating part of the
stabilizer and immediately begin to
revolve and move slowly towards the discharge
outlet with progressive maceration.
Retention varies from 2.5 to 4 days
depending on the rate of feed.
650283
Lindstrom, R. A simple process for
composting small quantities of
community wastes. Compost Science,
6(1) -.30-32, Spring 1965.
An experimentally-tested process to
achieve an aerobic biological change in
organic wastes is described. Wastes are
deposited into a naturally-ventilated
chamber. They move by gravity to a
second chamber at such a speed that the
wastes are substantially decomposed when
they reach it. The tank is divided by
vertical partitions into two or more
chambers, the upper chamber serving as
a receptacle for the feces, the next
one holding kitchen and garden refuse,
and the lowest chamber serving as
storage for the finished compost. The
chambers are connected through
ventilation holes in the partitions and to
the outside air through air vents. An
aerobic biological change in wastes of all
kinds is achieved with manure as an
end-product. All this is done without
mechanisms and without the addition of
chemicals or water. The arrangements can
be connected directly to the house or
building, serving as a toilet, garbage
container, an apparatus for biological
conversion, and collection and storage
place for the converted wastes. The
only costs are for the initial construction.
The invention is used primarily in areas
where no sewage treatment plant is
available. Most of the tank is below
ground level. Aeration of the wastes is
of primary importance in the decomposition
and determines the planning.
65-0284
McLemore, L. Houston sets up research
program for wastes. Compost Science,
6(1):9-10, Spring 1965.
The Garbage Committee of the City of
Houston researched the garbage problem
in their city and presented a report on
the disposal of residential, commercial,
and industrial waste. Their old garbage
dump grounds were being depleted at a
rapid rate, and their incinerators were
beyond repair. With incineration there
is a residue of ash which must be
landfilled, and landfilling is not
desirable in low, flat areas where the
water table is so close to the ground,
as is the case in the Houston area.
The committee felt that composting or
mechanical methods merited a research
and development program, as composting
eliminates odors, rodents, flies, and
provides a useful, marketable, and
soil-building product. Private enterprise
could invest money in this program with
he City guaranteeing a specific number of
tons of garbage per day. A notice was
then placed in the daily newspapers
inviting bids for construction, maintenance,
and operation of a plant or plants with
a capacity of 200 tons per day, and four
companies were recommended by the
Committee. Study indicated that
locating the plants less than 20 minutes
from the end of a collection route would
save the taxpayer thousands of dollars.
These plants, along with the 800-ton
incinerator now under construction, will
process more than 2,400 tons of garbage.
65-0285
Make compost now. The Compost Society
Journal, 24(2):9-11, Apr.-May 1965.
When crops are being harvested, nature's
bounty (fallen leaves) are everywhere
and crop residues are there to utilize;
this is an ideal time to make compost.
First consider what materials are
available and the greater the variety,
the better balanced the compost will be.
Any organic material may be used. The
stack should fill the bin rather than
partially fill it. The job should be
completed in one operation. The bin or
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0283-0289
container is a matter of one's own choice.
The sequence to be followed is to: (1)
place the bin in a position of easy access;
(2) dig or fork over the area to be
enclosed; (3) place a layer of coarse
materials as the base; (4) thoroughly mix
on the ground and dampen a layer of weeds,
grass clippings, or related material; (5)
cover the layer with animal manure or some
activator; (6) continue building the
layers and, after lightly tamping and
watering, seal with soil, sawdust, or
straw; (7) cover with any material that
will shed water; and (8) dismantle the
container. If the materials are in small
lengths, the breaking down process will be
accelerated. In three or four weeks
time the bin should be set up again and the
stack turned into it. One turning should
be enough, but the more turning, the
faster the compost matures.
and outside storage. A final grinder
is provided for bulk shipments. This
municipal project will cost around $2.60
per ton of input to operate the plant.
Arrangements have been made to market the
end products so that the City will make a
profit on the operation.
65-0288
New compost plant for Cheadle and Gatley.
Public Cleansing, 55(12) -.667-670, Dec.
1965.
A discussion on a new compost plant for
Cheadle and Gatley, Britain is presented.
Pre-separation of paper for salvage,
Insect-0-Cutors for fly control, space
heating of picking areas, lack of nuisance
from glass in the compost, and dry-weight
analysis of the compost are discussed.
65-0286
Maystre, Y. Are bad odors always concomitant
with a composting plant? Public Cleansing,
55(9):531-532, Sept. 1965.
A composting plant in Villette, Switzerland,
processes wastes from eight municipalities
and sludge, dehydrated to a 55 percent
water content, from the adjacent
biological sewage purification plant. To
prevent odor fermentation, gas
collected at the production points in
the plant is blown into buried pipes.
The soil acts as a filter. Results are
better in sandy soil than clay.
65-0287
Mobile, Alabama builds 300-ton-per-day
compost plant. Compost Science, 6(2):32,
Summer 1965.
In March, 1965, Mobile, Alabama, had a
contract for about $1,100,000 to construct
a compost plant scheduled for completion
in August, 1965. The plant is designed
to handle 300 tons of refuse per day, 6
days per week. Incoming trucks will be
weighed, driven up a ramp where refuse
will be dumped into a receiving hopper
and conveyor. As refuse moves, paper and
rags will be salvaged; cans and ferrous
metals will be removed magnetically
and processed for sale. Glass will be
removed and ground. The plant will have
a primary and secondary grinder. After
secondary grinding, moisture will be added,
and the compost will be baled for inside
650289
Reeves, J. B. Studies of sewage sludge
and sawdust compost. Compost Science,
6(2):12, Summer 1965.
Studies were conducted in regard to the
transmission of Salmonella and Shigella
by composted sewage sludge as a fertilizer
and soil conditioner. Early studies had
indicated that the disease producing
Salmonella and Shigella were not destroyed
by the temperatures reached in the
sawdust-sludge type of composting
mixture. Studies involving moisture
content of the composting mixture,
humidity, temperature of the environment,
and a continuous record of temperatures
inside the composting windrows, were
initiated. The main factors influencing
attainment of high temperatures in the
windrows were the moisture content and
carbon-nitrogen ratio of the composting
mixture. Studies were initiated to
determine the amount of supplementary
materials necessary to insure the
attainment of adequate temperatures in
composting mixtures. Molasses in
varying amounts from 5 to 50 percent was
utilized, and the results indicated that
a temperature of 140 F was not attained,
due to the raising of the moisture content.
Paunch manure was tested, and Salmonella
were isolated regardless of the amount
of manure used. When well rotted
barnyard manure was used it was found
that at least 15 percent of the manure
was used necessarily for a temperature
of 140 F or greater. No disease-producing
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Composting
bacteria could be isolated from those
piles. It was concluded that sustained
temperatures in excess of 140 F are
necessary for the production of a compost
containing sewage sludge and sawdust which
is safe for use as a fertilizer and soil
conditioner.
65-0290
Refuse composting plant at Stuttgart,
Germany. Compost Science, 5(3) : 1 0 .,
Autumn-Winter, 1965.
In the suburban area south of Stuttgart,
Germany, a composting plant was
constructed to serve as a large-scale
experiment for about 100,000 persons. Not
all of the product is used by agriculture,
the refuse being suitable for use as fill.
The plant operates under the Dorr-Oliver
(rasping system with windrow composting)
system having: a 120-cu m refuse bunker,
the usual magnetic separators for cans and
scrap iron, hand separation of
noncompostable materials, a D-0 rasping,
machine and ballistic separator for the
inert materials. The entire plant is in
one building and has available a 4,000-sq
m composting field. An important difference
from other plants is an incinerator with a
special grate built by the Esslingen
Machine Works which provides greater
capacity than the ordinary vertical
furnace. The 1 - to 1^-ton per hr furnace
permits the burning of large quantities
of industrial wastes and does away with
the tedious sorting of material on the
conveyor belt from the grinder. This
type of combination plant is suitable
to the needs of a middle-sized city
where it is impossible to solve the total
refuse problem by composting alone. Final
judgement about its operation must await
a long period of operation, with some
technical improvements to be made in
composting and incineration operations.
65-0291
Refuse reclamation plants. The Indian
and Eastern Engineer, 107:476, July
1965.
Westinghouse Electric Corporation has
developed a new process by which refuse
wastes can be processed in a swift,
inoffensive, silent, and invisible manner
into useful arid marketable forms. The
process involves housed 'light industrial'
plants which reclaim garbage rather than
destroy it. After marketable items in
the garbage have been screened, remaining
objects are pulverized and ground, and
then fed into a six-cell digestor section.
Here refuse decomposition is accelerated
by accurate control of moisture and
temperature. The finished compost is
a good organic soil conditioner. There
is no ash produced, and everything that
the salvage compost process manufactures is
useful. Another possible benefit from
the process lies in the fact that the
sewage sludge can be used to moisten the
material that is to become compost.
65-0292
Rose, W. W., J. E. Chapman, S. Roseid,
et al. Composting fruit and vegetable
refuse. Compost Science, 6(2):13-15,
17-25, Summer 1965.
The results of a preliminary investigation
in 1961 indicated that composting offered
a feasible and esthetically acceptable
method for disposal of high-moisture
wastes, such as fruit and vegetable solids.
Dry materials, such as municipal compost
or rice hulls can be used to absorb the
moisture from fruit waste solids. The
optimum initial moisture concentration
was 60 to 65 percent. Grinding the
fruit shortened the time required for
stabilization of composted unground fruit.
Aerobic conditions were maintained by a
turning schedule. The initial low pH
of the fruit compost mixtures appeared to
be the cause of an initial lag in
development of desirable microbiaL flora.
Of the dry mixtures used, municipal refuse
composted bv the Dano Process and rice
hulls performed satisfactorily.
Bin-composting studies were continued
during 1962 to test the performance of
various dry materials in the compost
mixture, and the effect of periodic
additions of fruit waste was studied.
Biological decomposition proceeds most
rapidly at thermophilic temperatures, and
the removal of moisture by evaporation is
maintained at the highest rate of
decomposition. A water extract of the
compost contained a heat-stable substance
inhibitory to spore germination. The
results of the investigations indicated
the feasibility of composting as a means
of disposal for high-moisture fruit and
vegetable wastes. There was an absence
of odor and fly problems. Because of the
85 percent moisture content, the evaporation
during the composting and drying produced
large weight and volume losses in the
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0290-0296
initial mixture. Chemical additives such as
lime and urea produced a more favorable
environment for microbial growth. The
stabilization of wastes decelerated with
subseauent waste additions. Savings in
time and labor would result if the compost
could be aerated by injection of air. The
1964 study will determine the effect
of the compost process on pesticides.
65-0293
St. Petersburg, Fla., to build composting
plant. Compost Science, 6(1):10, Spring
1965.
The City of St. Petersburg, Florida,
entered into a contract with Sacs, Inc.,
to finance, construct and operate a
105-ton per day composting plant. Very
rigid performance specifications were
set. The City Manager estimates that
the plant will be under construction by
the end of June 1965, and completed
by the end of June, 1966. Sacs, Inc.,
was the low qualified bidder with a
per ton cost of $3.25. Westinghouse
Electric is designing the plant. The
original bids specified as 20-year
contract for processing system that was
completely enclosed, and free from noise,
odor, and dust conditions. Open windrowing
will not be permitted. Products offered for
sale will contain no pathogenci organisms
and will not reheat upon standing
nor cause odors.
65-0294
Sanford, C. F. Elmira to try composting.
American City, 80(7):93-94, July 1965.
Elmira, New York, has signed a contract
with National Organic Corporation at
Atlanta, Georgia, to compost 20,000 tons of
refuse per year at $4.35 per ton. The
corporation assumes the risk and finances
the plant thereby staking its reputation
on the venture. Presently Elmira spends
$117,000 per year for refuse disposal,
and the estimated cost under composting
will be $87,000 per year. The plant
will cost the corporation $650,000 to build.
65-0295
Schaffer, H. And Jersey keeps on composting.
Compost Science, 6(1):14-15, Spring 1965.
Jersey, the 45-sq mile island between
Britain and France, has a. waste conversion
plant which converts both sewage and
household rubbish into fertilizer. This
was the result of its two main sources of
income--holiday traffic and agriculture--
demanding more effective waste disposal. The
discharge of sewage into the sea was
impractical because of ocean currents
carrying it back to the beaches, and the
incineration of rubbish was equally
unsatisfactory. There was an urgent need
for fertilizer for Jersey's two main
crops, tomatoes and potatoes. All of
the island's organic wastes are converted
and utilized on the land. At first
there was opposition to this, but, with
the substantial improvement in crops, it
became widely accepted. The compost was
found to be richer in the trace elements
and contained several antibiotics, and,
in addition, controlled the eelworm, a
nematode which attacks both potatoes and
tomatoes, A reclamation of wasteland
has resulted, the compost being used
to create gardens on virtually pure sand.
Sewage sludge is brought from the sewage
plant where the conventional treatment by
sedimentation and bio-aeration takes place.
It is then mixed with the compost before it
passes through the fermentation cells. A
purified effluent, rich in nitrogen, is piped
to the compost plant and added to the
compost.
65-0296
Schulze, K. L., V. Brown, J. Houser,
et al. Composting (Panel). In
Proceedings; Technical and Planning
Aspects of Solid Wastes, Columbus, Ohio,
Sept. 1965. Ohio Department of Health.
p.M-1 to M-38.
The criteria for design and operation
of a successful commercial composting
plant are: an acceptable aesthetic
appearance; air pollution must be
considered in site selection along with
the economics of the haul. Slides were
shown of a pilot plant and its components.
In order for a plant to become economically
feasible in any city, the city must be
willing to pay for the service on a
substantial basis. The successful
commercial plant will be improved. The
Fairfield-Hardy Digestor, a patented device
for converting garbage and refuse, sanitary
sludge, and animal and other waste into a
usable compost or soil conditioner, is
described. The digester can be fed
continuously or intermittently and
operates completely in a thermophilic
environment. Automatic controls to
regulate and record the temperature and
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Composting
oxygen requirements are available. Wet
pulping and dry grinder systems are used.
The components were shown in slides. The
history of the International Disposal
Corporation is traced. The patented
aerobic process involves grinding and
preparing to form a somewhat homogeneous
material which is fluffed, aerated, and
in 3 days re-ground to a finer size to
allow decomposition. After 6 days it
is again ground and prepared for marketing.
It can be sprayed as a germination base
for grass seed and later decomposes as
a soil conditioner. This is a completely
nuisance free, reliable, and economical
method of refuse disposal. The height
and duration of temperature required
for the composting process are discussed.
Public health dictates that compost
containing feces be subjected to
continuous temperature of 140 F for
at least 5 days. The difficulty
arises in ensuring that all of the material
reaches this temperature. Several
European plarts are described and pictures
shown.
65-02S7
Schulze, K. L. Composting as a waste
disposal method. In Proceedings;
Technical and Planning Aspects of Solid
Wastes, Columbus, Sect. 1965. Ohio
Department of Health. p.L-2 to L-13.
Data is presented on the garbage to be
disposed of in the United States and the
methods used by American cities. There
is no city which composts garbage on a
full scale basis. Cases of composting
plants operated privately and which have
failed are given. Two reasons were:
the idea of large profits dominated the
enterprise, and unsubstantiated claims as
to the value of the product were made. The
composting plant in use in Holland is
described. The biochemistry involved in
the decomposition of organic waste material
is described in detail: basic oxidation
equation, the bacteria, a temperature-time
curve, and the effect of moisture content
on the activity of the compost. The
quantitative aspects of the process were
investigated by using a rotating cylinder
made from Lucite and having a capacity of
15 to 20 Ib of raw garbage. The oxygen
consumption per gram initial volatile
matter per hr and the changes in this
oxygen consumption rate with temperature,
and with different mixtures were recorded.
The data showed that during the
thermophilic phase air had to be supplied
at a rate of about 14 cu ft per minute
per ton of volatile matter in order to
satisfy the demand. A controlled
continuous supply of feed material and
air with controlled moisture ranges to
maintain a composting process continuously
in the thermophilic phase was tried. This
would result in higher efficiency of the
process and greater sanitary safety. The
combination of dewatered sludge and garbage
to be disposed of by composting is
discussed.
65-0298
Schulze, K. L. The Fairfield-Hardy
composting pilot plant at Altoons, Pa.
Compost Science, 5(3):5-10, Autumn-Winter,
1965.
The Fairfield-Hardy composting pilot
plant at Altoona has demonstrated on a
full-scale basis that it is possible to
operate a mechanical composting unit
continuously in the thermophilic phase,
i.e. at a temperature range between 130
and 175 F, and to produce a sanitary
compost which is free from obnoxious
odors and does not attract flies or
rodents. The process consists of pulping
raw garbage in a wet pulper, dewatering
the pulp in a screw press to about 75
percent moisture, and then windrowing
the dewatered pulp from a period of at
least 2 months. After that, the compost
is pelletized and flash dried in a heated
rotating drum. The end product is
a very uniform brown granular material
which is sold as an organic base for
fertilizer production. The wet pulper
consists of a 6 ft diameter stationary steel
bowl equipped with a rotating steel plate
at the center of the bottom. The plate
is studded with specially hardened
steel teeth. So far, only air dried
digested sludge has been used; however,
there is little doubt that raw or
digested sludge, which has been dewatered
by vacuum filtration of centrifugation,
etc., can be composted in the
Fairfield-Hardy unit.
65-0299
Spohn, E. Glass in compost. Staedtehygiene,
16(6):129-134, June 1965.
The popular belief that glass in compost
is less sharp-edged made us look into
this matter more closely. First, the
literature was scanned for previous
findings on the decomposition of glass.
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0297-0302
An article by Oberlies and Pohlmann,
on the effects of microorganisms on clay,
cites twenty authors who dealt with
bacteria attacking silicates. As early
as 1913 Basalik made extensive experiments
by growing cultures of bacteria on
silicates such as feldspar, mica,
olivine, etc. He measured the decomposed
amounts and found that their magnitude
depended on the kinds of bacteria used
as well as on the silicate material.
Oberlies mainly investigated the attack
of microbes on optical glasses. According
to Rohde not only bacteria attack glass
but also lichens and fungi. Schatz found
that acids are not involved in the chemical
decomposition process but complex
metal-organic compounds. The present
authors conducted experiments to see how
fast glass is attacked in a waste composting
process. In mulch, no biological
decomposition can be expected because
of the rapidity of the process. Polished
glass plates were put among the waste
layers and subjected to a regular composting
process. After 3 months, the glass
plates had blunt oval pits in a chain
like arrangement. The pits had a diameter
of approximately 0.5 to 1 micron, their
depth was 0.25 micron. Scratches in the
glass plate had been attacked more heavily.
This observation leads to the conclusion
that sharp edges and tips are attacked
first and more strongly, which confirms the
popular belief stated in the beginning.
Nineteen microphotographs of glass
surfaces are reproduced. (Text-German)
65-0300
Stirrup, F. L. Composting. In Public
cleansing; refuse disposal. Oxford, The
Institute of Public Cleansing, 1965,
p.72-86.
Composting is used for providing feed for
impoversihed soil, disposing a large
portion of refuse, and disposal of
sewage sludge. Humus gives soil good
texture and pervents erosion. There
is a breakdown of organic matter by
bacteria and fungi under aerobic
conditions. Different systems and processes
are described. The Indore process
alternates layers of straw and dried
vegetation with layers of manure. The
Dumfries system in inside a covered
plant. The Jersey system has a plant
of six stories and maturing sheds. The
Dano process uses hoppers and bio-stabilizers.
The Beccari process has an initial anaerboic
breakdown in sealed tanks followed by a
partial aerobic process. The Verdier
process draws air from top to bottom and
sprinkles with water or liquid sewage.
In the 'Biotank' process refuse is
ground to reduce volume and thoroughly
mixed. Innoculants containing
microorganisms assist fermentation. Bristol
uses the Prat system where special attention
is paid to aeration. Refuse in the 'VAM'
refuse disposal system is sprayed with
water containing a bacterial innoculant.
There is revenue from by-products and
the product itself if the compost is
free from contraries. Growers have
requested both finely ground and coarse
material. A pH value of 8 to 9, and a
carbon-nitrogen ratio of 20:1 is a basic
guide.
65-0301
Summary of 1964 field scale composting
studies. Compost Science, 6(2) :25,
Summer 1965.
The specific aims of the 1964 Field Scale
Composting Studies were the investigation
of materials handling problems, comparison
of forced aeration of windrows vs.
aeration solely by mechanical turning,
and the effect of composting on pesticides.
In investigating materials handling
problems associated with the collecting,
grinding, and distributing of fruit waste
to the windrows, a two-sectioned concrete
reservoir was constructed to contain the
solid waste as hauled from a cannery and
the fruit waste after grinding. Upon passage
through the grinder, the fruit waste was
reduced to a pulpy consistency which
appeared to be pumpable. In testing forced
aeration, two stationary windrow walls
were constructed on the asphalt surface,
containing a 30 cu yd mass of rice hulls.
Forced aeration of one windrow was
accomplished by imbedding perforated
copper pipe beneath the asphalt surface.
Air was supplied by a positive displacement
rotary blower. Both windrows were mixed
after the addition of fruit waste by a windrow
turner.
65-0302
Teensma, B. Guidelines for composting
raw ground refuse. Compost Science,
5(3):26, Autumn-Winter 1965.
Guidelines for composting raw ground
refuse, based on the experiences of the
Dutch compost plants, are provided.
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Composting
Compost windrows should not be higher
than 2 m, and the tops should be rounded
or roof-shaped to permit rain runoff. The
windrows must be separated and the area
well drained to avoid puddle formation
after rains. The moisture content of
the raw refuse at the time of stacking
must be between 50 and 55 percent. The
interior of all windrows must be checked
every week. When zones have been formed,
the windrows must be turned (every 2-3
weeks) and checks must be continued after
turning. As soon as new zones form,
turning will need to be continued until
they disappear. When this stage is
achieved, the compost is finished and ir.ay
be piled in large stacks. The use of a
belt conveyor with a nail covered concussion
mill as a turning machine is recommended,
as well as an addition of 10 to 20
percent by volume of ripe compost or peat
to the raw refuse.
65-0303
$300 million for non-farm fertilizer.
Compost Science, 5(3):15, Autumn-Winter
1965.
Today the U.S. non-farm fertilizer market
has a value of $300 million--$157 million
from home gardeners, plus $143 million
from professional landscapers, parks,
etc. Non-farm fertilizer use has grown
at the rate of about 10 percent per year
since 1960, with major growth occurring
in California, Texas, Florida, the Northeast
and East North Central areas. About
25 percent is sold in garden centers,
20 percent in hardware stores, 10
percent in discount and department
stores. Organic fertilizers comprise
one-third of the fertilizers sold on a
tonnage basis.
65-0304
Toward a healthy solution for waste
problems. Compost Science,
6(2):3, Summer 1965.
The developments concerning the safe
disposal of waste products are reviewed.
New disposal methods are rapidly being
sought for the 4^ Ib of solid wastes that
the average American produces each day.
Congress is now considering the $43
million Solid Waste Disposal Act, which
will provide for evaluation of such new
approaches to garbage handling as
large-scale composting. The Solid Wastes
Composting Research and Demonstration
Project sponsored by the Tennessee Valley
Authority and the Public Health Service
provides for a full-scale demonstration
composting plant to be designed and uilt
within the next year in a city located
in the Tennessee Valey area. Houston,
Texas, will soon have the greatest number
of and the largest composting plants
of any U.S. City with three companies
submitting contracts for plant construction.
In Mobile, Alabama, a 300-ton per day
compost plant which will treat refuse and
sewage sludge is being constructed. In
Brooklyn, New York, a compost plant was
formally opened utilizing a digester
which had been handling 15 tons of
restaurant food waste per day. Other
cities, where plants are now operating
or will soon be built, include: Altoona,
Pennsylvania, St. Petersburg and Largo,
Florida, Wilmington, Ohio, and New Orleans,
Louisiana. The Solid Waste Disposal
Act now before the Congressional Committee
on Interstate and Foreign Commerce proposes
authorization for: a national research
program on improved methods of solid
waste handling and disposal, technical
assistance to state and local governments,
matching funds for demonstration projects,
and training.
65-0305
Visser, S. A. Decomposition of organic
materials in the tropics. Compost Science,
5(3):27-29, Autumn-Winter 1965.
In Uganda, about 15,000 sq miles are
covered with tropical swamps of which only
225,000 acres are suitable for reclamation.
A research team has investigated the
properties of the peats and the processes
occurring in them for the remaining 14,649
sq miles of swamps. About 60 percent of
the vegetation of the swamps consists
of Cyperus papyrus, the greater part of
which decomposes where it grows. Three
types of samples were investigated: (1)
dried papyrus together with various
additives, decomposing in vitro; (2)
dried papyrus and various additives,
contained in baskets of fine nylon gauze,
which were left to decompose in natural
papyrus swamps; and (3) peat core samples
from deep natural papyrus peat deposits
with depths of over 10 m. In type 1, the
components forming the gas mixture, as read
daily from a calibrated gasometer for
1,200 days, were found to be methane,
carbon dioxide, hydrogen, and traces of
carbon monoxide and ethylene. The methane
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0303-0308
content appeared to increase with
progressing fermentation. The microflora,
and particularly the aramonifiers and
denitrifiers, were found to be highly
active. In type 2 the amounts of fats
and waxes were of the same order for all the
samples investigated. The alcohol extracts
showed values as much as five times larger
than those obtained with other solvents.
Both the carbon and nitrogen contents of the
mixtures increased during decomposition, but
the C/N ratio decreased, as did the fulvic
acids. In type 3 the nitrogen content
decreased with the depth of the sample but
the C/N ratio increased after an initial
drop, while the fulvic acids showed the
smallest change with depth. Very rapid
decreased in depth were noticeable among
the microflora.
65-0306
Weinburgh, H. B. Composting; sanitary
disposal of wastes. Atlanta, Ga. U. S.
Department of Health Education, and
Welfare, Communicable Disease Center,
1965. 32 p.
Research has shown the feasibility of
composting municipal wastes. Proper
aerobic, thermophilic composting produces
the time-temperature conditions required
for pathogen destruction. Composting
costs are similar to those of the
sanitary landfill and less than those of
incineration. Composting produces a
humus capable of improving poor land at
the rate of 1 acre per 10,000 persons per
day. The aerobic and anaerobic
decomposition of organic matter is
described. Factors affecting composting
include refuse sorting and grinding,
carbon/nitrogen relationship, moisture
content, placement of materials,
temperature, aeration, mixing, climatic
conditions, nitrogen conservation, and
composting time. The unit processes
of a city composting plant are refuse
reception, salvage separation and
preparation, compost preparation,
decomposition and stabilization, and
market preparation. Methods of composting
on farms are reviewed. Selected references
are appended.
65-0307
Weinburgh, H. B. Decomposition of organic
matter. In Composting; sanitary disposal
of wastes. Atlanta, Ga., U.S. Department
of Health, Education, and Welfare,
Communicable Disease Center, 1965. p.3.
In aerobic stabilization, bacteria, fungi,
and actinomycetes, which use oxygen,
feed on the organic matter and develop
cell protoplasm from the nitrogen, phosphorus,
some of the carbon, and other required
nutrients. It the excess of carbon over
nitrogen in organic materials being
decomposed is too great, biological activity
diminishes and the process is slowed. When
the ratio of carbon to nitrogen is too low,
excess nitrogen is released in ammonia.
Under favorable conditions some of the
excess nitrogen may be oxidized to nitrates.
There are no disagreeable odors produced
in the aerobic process when adequate oxygen
is available. If the organic material is
in a pile or otherwise arranged to provide
some insulation, the temperature during
fermentation will rise to over 158 F.
If the temperature exceeds 150 to 160 F,
bacterial activity is decreased and
stabilization is slowed. Putrefactive
breakdown of organic material occurs
anaerobically. Anaerobic bacteria use
nitrogen, phosphorus, and other nutrients
in developing cell protoplasm, but reduce
the nitrogen-containing compounds to
organic acids and ammonia. The carbon no_t
used in cell protoplasm is liberated mainly
in the reduced form as methane.
65-0308
Weinburgh, H. B. Sanitary and agricultural
aspects. In Composting; sanitary disposal
of wastes. Atlanta, Ga., U.S. Department of
Health, Education, and Welfare, Communicable
Disease Center, 1965. p.3-6.
The destruction of pathogens and parasites
is an important aspect and problem of
composts containing contaminated materials.
Aerobic composting at high temperatures is
effective in destroying these organisms.
The high temperature zone usually extends
only to within 4 to 8 in. of the surface
and turning the outer material to the
center is necessary to insure pathogen and
parasite destruction. When materials
attractive to flies are composted, some
of the larvae will move to the outer cool
areas and continue their life cycles.
Frequent turning of the outer layers
into the center is effective in destroying
eggs, larvae, and pupae. Humus from manure
and garbage contain some nitrogen,
phosphorus, potassium, and trace elements
but the amounts are too low for classification
as fertilizer. Humus has desirable
characteristics in addition to nutrients.
The organic acids produced combine with
phosphates in a form readily available to
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Composting
higher plants. Both phosphorus and
nitrogen are involved in a storing effect.
The humus may also contribute to increased
nitrogen-fixation in the soil from nitrogen
in the air. Compost is much more valuable
for its physical effects on soil than for
any chemical nutrients it may add. It
improves soil structure and lessens wind
and water erosion. The high temperatures of
aerobic composting destroy viability of
weed seeds.
65-0309
Weinburgh, H. B. Factors affecting
composting. In Composting; sanitary
disposal of wastes. Atlanta, Ga., U.S.
Department of Health, Education, and
Welfare, 1965. p.6-15.
Removal of salvable and non-compostable
materials is usually necessary. Grinding
the raw material renders it more susceptible
to bacterial invasion, produces beneficial
initial aeration, and assists in
homogenizing the material. The initial
aeration, and assists in homogenizing the
material. The initial C/N ratios of some
composting materials are listed. Aerobic
decomposition can proceed at any moisture
content between 30 and 65 percent if
adequate aeration is provided. The
material in aerobic compost piles should
be loosely stacked. Five to 6 ft is
about the maximum height for any material
and 3^ to A ft is the minimum.
Decomposition proceeds much more raoidly
in the optimun temperature range, 120 to
160 F. The frequency of aeration or
mixing and the amount of aeration or the
total number of turns are governed primarily
by the moisture content and the type of
material. Mixing at frequent intervals
during the first 10 to 15 days of aerobic
composting achieves about the same degree
of stabilization as making the same number
of turns over a longer period. Climatic
conditions, particularly temperature, wind
and rainfall, influence the composting
operation when using windrow, piles, or
stacks. Nitrogen can be lost be leaching,
but the major loss comes from the escape
of ammonia or other volatile nitrogenous
gases. A material with an initial C/N
ratio of 30 to 50 (moisture approximately
70%) can be stabilized in a period of
time from 10 to 16 days. Compost can be
tested and judged on the basis of
temperature, moisture, appearance, odor,
pH, and maturity.
650310
Keinburgh, H. B. Methods and planning for
cities. In Composting; sanitary disposal
of wastes. Atlanta, Ga., U. S. Department
of Health, Education, and Welfare, 1965.
p.16-26.
Factors to be considered in the analysis
and planning for the establishment of a
plant to compost city wastes are listed.
The unit processes in large scale
composting plants are: reception of the
refuse; sorting and preparation of the
salvable material for sale; preparation
of the compost (shredding, pulverizing,
or screening to facilitate decomposition);
decomposition or stabilization to reduce
C/N ratio, to destroy pathogens, parasites,
and weed seeds, and to control fly
breeding; and preparation for the market
(final grinding and bagging). The many
different finds of grinders and shredders
include: swing hammers, rigid hamers,
shredders with rigid bars and either spring
or weight loader breakers, cutters or
chippers, mills, wet pulpers followed by
presses, crushers, rasps, and slowly
rotating drum mills. The types of
composting methods that have been used
are: pits or cells, windrows or stacks,
and vertical or horizontal enclosed
digesters in which the refuse is mixed
and aerated mechanically. The Dano,
Naturizer and Jersey processes are
described in detail. Comparative costs
of enclosed mechanical digester and
windrow composting operations are listed.
65-0311
Weinburgh, H. B. Methods for farms. In
Composting; sanitary disposal of wastes.
Atlanta, Ga., U.S. Department of Health,
Education, and Welfare, Communicable
Disease Center, 1965. p.27-28.
A farm seldom has enough manure and litter
to build, at least once a week, an
individual compost stack large enough to
maintain high temperatures. The size
and number of stacks to be used depends on
the amount of manure and waste available.
Stable manure is made of three main
components: bedding or vegetable-matter
litter, solid excreta, and urine. Stable
manure in a fresh condition contains about
70 to 80 percent moisture. A compost
pit can be built of concrete or masonry.
The area sould be such as to provide the
desired volume when the pile of material
to be composted is 4 to 5 ft high (inside
measurements about 8 ft by 8 ft). It is
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0309 -0314
desirable to have a concrete or masonry
slab under a composting stack and a sump
for catching the drainage. Coarse cellulose
material (straw, corn or can stalks) on
the bottom of the stack is essential
for retention of nutrients and development
of humus. The cellulose layer should be
at least 12 to 18-in. deep so that it will
pack to no less than 3 or 4-in. Any type of
organic litter can be added to the manure
pile and composted increasing the amount
of humus and decreasing nitrogen loss.
Poultry manure can be composted by removal
to a compost stack or composted under the
cages. It is necessary to aid cellulose
litter to increase the strength of the
material to maintain the stack, to improve
the C/N ratio, to increase porosity for
aeration, and to absorb ammonia, moisture,
and odors.
650312
Weinburgh, H. B. Summary. In Composting;
sanitary disposal of wastes. Atlanta,
Ga., U.S. Department of Health, Education,
and Welfare, Communicable Disease Center,
1965. p.29-30.
The three approved refuse disposal methods
available to a municipality are sanitary
landfill, incineration, and composting.
A composting plant should be capable of
accepting almost everything that is
delivered. The market value of compost
compares favorable with that of a good
farmyard manure on a weight for weight
basis. Since refuse disposal is an accepted
municipal responsibility, composting should
be considered by the municipality as a
refuse disposal method, rather than a method
for supplying an agricultural need. Selling
only part of the product at a very high price
provides no solution to the overall disposal
problem. The overall cost of a refuse
composting plant will be more than that of
a sanitary landfill, but less than that
of an incineration operation. The
construction costs of a full-scale
compost plant for a city of 120,000
would be about $435,000 to 560,000.
The operating and amortization costs of
a mechanical composting plant for a city
of 30,000 were estimated to be about
$4 per ton of mixed refuse, after
deducting revenue from the sale of
salvage (about $3 per ton of refuse).
Adequate operation of a hygienic composting
process requires hiring of a consulting
engineer to design the plant, the designing
and constructing of a compost plant suited
to the particular needs of the municipality,
and having a qualified supervisor on the
job from the beginning.
650313
Wiley, J. S., and 0. W. Kochtizky.
Composting developments in the United
States. Compost Science, 6(2):5-9,
Summer 1965.
The alarming rate of increase in the
population (doubled by 2,000) and the
increase in per capita refuse production (now
about 4.5 Ib per capita per day) together
create a formidable problem. Most of the
population growth will be in cities and
their surrounding urbanized areas so the
available land for ultimate disposal of
refuse will become reduced. The increase
in volume of refuse is far greater than
the increase in weight, and the greatest
increase is in low-density combustible
rubbish, mostly paper and plastics.
Garbage and ashes are slightly reduced
in quantity. Many cities now using dumps
will have to reduce the volume of their
refuse to conserve land areas. Burning,
garbage grinding, salvage, and composting
are methods to reduce volume. The calorific
content is increasing but the nutrient
content, of importance in composting, is
decreasing. The composting plants in
Altoona, Pennsylvania; Largo Florida;
Norman, Oklahoma; Phoenix, Arizona;
Sacramento County, California; San
Fernando, California; Springfield,
Massachusetts; Williamston, Michigan;
and Wilmington, Ohio, are described and
the technical problems in their operation
discussed. Houston's installation is
described. A proposed TVA-PHS research
and demonstration plant is mentioned.
65-0314
Word of caution from Kingston, Jamaica.
Public Cleansing, 55(2) :103, Feb. 1965.
A composting plant, using part of the
Kingston, Jamaica, refuse has met with
financial difficulties. The plant,
sponsored by the National Organic
Corporation of Atlanta, Georgia, now holds
1/10 instead of the projected 1/3 of the
city's 220,000 tons of annual waste. The
Corporation originally offered to pay the
city for its refuse at $0.15 per ton of
compost produced, but has now asked a
subsidy from the city to offset financial
difficulties. The nutritional value of
the compost was too poor for fertilizer,
and it has been difficult to find a local
market among cane farmers.
69
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REDUCTION
65-0315
Bopp, R. A new machine for shredding bulky
waste. Schweizerische Bauzeitung, 83(6):94-95,
Feb. 11, 1965.
Bulky waste can hardly be burned or composted
without crushing or shredding it first. For
this purpose a new waste shredding machine
has been developed by the company Von Roll
AG., Zurich. The new machine is capable of
shredding all the various kinds of bulky
wastes automatically. Its capacity varies
between 120 and 200 cu m per hr. The large
horizontal input opening of 3 by 3.4 m makes
loading simple. The machine consists of two
steel frames joined together. The stationary
frame has seven parallelly arranged sectional
iron supports spaced one foot apart with
blades screwed to their edges. The movable
frame has two rakes, each made of 3 beams
which are connected by a horizontal member.
Two hydraulic cylinders move the rakes whose
beams fall into the spaces of the stationary
frame. The bulky waste is caught by the
blades and minced. The movement is slow but
very powerful and almost noiseless. The
motor power is low, only 37 kW are required.
The machine takes any kind of bulky waste.
Since all forces arising in the shredder are
taken up by the structure of the machine,
the foundations need to support only the
weight of the shredder which is 28 tons.
Besides the crane operator no other personnel
is needed. The shredding machine is shown in
a photograph and a technical drawing. A
smaller machine with an input opening of 3 by
1.55 m is also available. (Text-German)
65-0316
Can/bottle crusher. Modern Sanitation and
Building Maintenance, 17(10):48, Oct. 1965.
'Crush-all' provides 17 tons of pressure to
crush cans with both ends in place--like juice
cans which have only been punctured. It
handles cans up to 5 quarts and bottles up
to 1 gal. Since operation is by a start-stop
switch, no operator training is required.
65-0317
Clippers counter Cleo debris. American City,
80(2) :36, Feb. 1965.
Miami Shores, Florida, had to place two new
brush chippers into operation to clean up the
brush debris left in the wake of Hurricane
Cleo. The chippers reduce the bulky brush to
as little as one-fifth its original volume
and shoot the debris directly into truck boxes ,
65-0318
Combs, W. H., and S. N. Craig. Waste disposal
methods - part I - pulping. Modern Sanitation
and Building Maintenance, 17(9):15-17, Sept.
1965.
Incineration is the most used method of
disposal but it only gives 95 percent
reduction in volume of loose non-compacted
burnable material. Incineration contributes
to air pollution. Balers require labor to
segregate materials since baling implies sale
of accepted salvage. By using a hogger or
shredder and blower with a baler, an automated
system can be developed, but this proves
undesirable if high dust and noise levels are
a problem. Also, metal separation must be
nearly 100 percent to avoid the hazard of
dust explosion. Garbage grinders are
excellent for food wastes, providing silverware
and paper is kept out of the meshing parts.
The pulping system consists of two parts: a
pulper and a waste extractor recirculator.
The pulping unit is basically a tank with
rotating impeller, recessed below the contour
of the tank itself making it non jamming. A
row of cutters permits tearing of nonpulpables,
which are mixed with general wastes. As it
is chewed small enough to pass through the
screen, it is pumped as a slurry of 2 percent
solids to the water extractor. Heavy
nonpulpables are separated by a combination
of centrifugal force and gravity and settle
in an opening in the bottom of the tank and
emptied. Material in the form of slurry is
pumped to the Hydra-extractor. The material
is squeezed to remove additional water. The
system provides an 80 percent reduction in
volume.
65-0319
Eases waste disposal.
37(6):112, June 1965.
Food Engineering,
An automatic, low cost refuse disposal system,
which processes 1 ,000 Ib per hr of paper,
packing material, food wastes, glass and
metal was developed by the Somat Corp. It
produces a semi-dry pulp reduced to about
10 percent of original volume. The unit also
lowers in-plant handling and maintenance,
provides a cleaner, relatively quiet operation,
and improves safety. The pulper, which is
schematically illustrated, is a tank with
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0315-0323
a rotating disk in its bottom. Metal and
glass fed to the pulper are separated from
pulpable refuse by centrifugal force and
gravity. Cans are normally reduced to about
75 percent initial volume and glass is
shattered completely. A brewery which
destroys up to 20,000 Ib of beer cartons a
day sells the pulp to a nearby roofing company,
but savings are experienced when handling as
little as 100 Ib a day.
65-0320
Gondard plant for Haarlem. Public Cleansing,
55(7):386-387, July 1965.
Haarlem has decided to use three Gondard
refuse reducers in order to utilize its
municipal refuse. Pulverized material from a
Standard Gondard Refuse Reducer is fed to two
Gondards where it is reground. These machines
are set at a throughput of 12 tons per hr,
which allows for the collection at Haarlem
which is about 100 tons per day. The entire
Gondard installation is mechanized.
65-0321
Greenway, W. F., and J. Farnell. Refuse
pulverising plant for Welsh Authority.
Surveyor and Municipal Engineer, 126(3826):19-20,
Oct. 2, 1965.
The Mountain Ash Urban District Council has
solved its waste disposal difficulties by
installing a Volund rotary refuse pulverisation
plant to serve its 16.5 sq miles of urban
population. The past practice of tipping has
been abandoned in consideration of its serious
deficiencies: fire outbreaks, fly infestation,
child trespass, and sheep trespass to tips
as a feeding ground. After considering
alternative methods of disposal, the Council
chose pulverisation because it provides a
material for landfill which prevents nuisances
normally associated with refuse tips. The
pulveriser has a capacity of 10 tons per hr.
The plant is centrally located, so that
maximum haulage distance is about 4 miles. A
brief description of the plant's operation
is included. Crude refuse is conveyed from
a 60 cu yd hopper to the pulveriser, while
salvage is collected by hand from the refuse
on the conveyor belt. The rotary screen of
the pulveriser leaves the refuse in three
sizes for storage hoppers. The whole plant
is centrally controlled. Fifty adjoining acres
should serve as a disposal site for about 40
years. The site layout includes a 30 ton
public weighbridge and an amenity welfare
block for employees. Capital costs should be
about fc74,500; operating costs are estimated
at fc9850 p.a. Householders have been provided
with a bin of 2 sq ft capacity to improve
domestic storage and facilitate conditions for
collectors.
65-0322
Low cost refuse compaction by wet drum.
Engineering, 200(5200):791, Dec. 17, 1965.
A refuse conversion plant, which passes the
refuse through a rotating pulverizer drum
and introduces water to break down fibrous
materials like paper and cardboard, is
described. The plant has a nominal capacity
of 45 tons per day and is based on a
cylindrical 8 ft diameter drum, 29 ft long,
carried in a frame and rotated at 11^ rpm.
The drum is charged with refuse through a
hopper and single loading throat and then
water is introduced by a metering pump to give
a moisture content of about 40 percent.
Flight plates on the inside of the drum elevate
the refuse through a large fixed crushing
cone which forces it further forward.
Pulverizing occurs in the first 12 ft of the
drum under the action of segmental steel
deflection plates; the refuse then passes
into the screen section and annular void and
then to discharge. Design throughput rating
is 1^ tons per hr and discharge is continuous.
The product from the drum is peat-like in
appearance and ready for covering a rubbish
dump. The plant and process are simple and
inexpensive, with the costs, including dump
operation, below 10s per ton for the first
7 years if the plant is rented. Another
feature is that when a dump is full the
plant can be easily moved to another site.
65-0323
Mobile balers. Waste Trade World, 106(16):9,
Apr. 17, 1965.
Mobile baling presses which are simple to
load and operate, and process a wide variety
of waste materials, are marketed by Funditor
Ltd., London. Three models are available, and
one of these is described and illustrated. It
can be operated with press button simplicity
and left to operate itself in complete safety,
enabling baling material to be assembled while
a bale is being produced. The platen is
actuated by a twin rack and pinions, giving
a total thrust of 1% tons. The thrust is
applied by a one-third hp motor running
at 950 rpm through a reduction gear mechanism.
An average bale measuring 14!« by 35 by 75 in.
takes about 6 minutes to produce.
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Reduction
65-0324
More about the Reno. Public Cleansing,
55(11) -.658-659, Nov. 1965.
The Reno refuse collection vehicle can
provide a well pulverized refuse by the time
it reaches the landfill. The vehicle is
manufactured in Denmark and consists of three
sections. These sections are combined by
flexible links so that the driver's cabin,
the outer skin of the body, and the rear end
move independently of each other. The
rotating drum container is fitted with
internal vanes which guide and macerate the
refuse. Revolution of the drurr can be in
either direction and at 45 rpm. Reversal of
the direction of rotation will discharge the
contents. A 400 liter water tank is attached
for moistening the refuse during pulverization.
Capacity is sufficient for a whole day's
operation.
crusher jaws compress containers to a fraction
of their former volume. For high-speed
crusher operations, opposing sets of
heavy-duty steel tracks converge and crush
the material. Speed of tracks may be
regulated to create tearing action In addition
to crushing. The output of the machines is
not fluffy, but rather of a dense consistency
resulting in efficient volume reduction of
bulky waste. A wide range of units is
available with horsepower ranging from 3 hp
to 100 hp. The construction and operation
of a standard machine is described. The
company also supplies completely engineered
systems to fit production or salvage
requirements.
65-0327
Package contract. Public Cleansing, 55(9):519,
Sept. 1965.
65-0325
New bottle breaking machine. Waste Trade
World, 107(2);22, July 10, 1965.
Three improvements incorporated in the latest
model of the 'Fortune' bottle breaking machine
are described. The drive is now by means of
a loose coupling which obviates the possibility
of damage to the motor bearings in the vent
of a strain taking place in the breaking unit
itself, and eliminates the possibility of
very fine glass dust getting into the motor
bearings. Use1 of the hardest manganese steel
available has also meant a much longer life
from the breaking unit. The rubber baffle has
now been moved up the tube to approximately
6 in, from the top which ensures that the
next bottle being put in will push the
previous one through, if by any chance Lt
has become jammed. The delivery tube also
has been lengthened and cranked to make it
impossible for operators to get their arms
into the tube while the machine is running.
A standard model, which is designed for
general use and can be fitted to any normal
dust bin, and a cabinet model are available.
65-0326
New waste reduction systems. Waste Trade
World, 107(1) :9, July 3, 1965.
A new range of waste reduction machines has
been introduced by CentriMast Corp.
Centriblast disintegrators handle cardboard
fiber, plastic, glass, metal, wood, rubber,
leather, etc. materials, alone or in
combinations. The heavy, reinforced
The Borough of Epsom and Ewell in Surrey has
contracted for a refuse separation and
pulverization plant on the Fermascreen
principle. This system pulverizes, dampens
and screens refuse in rotating drums and
involves minimum maintenance and power
consumption. It can also accept crude refuse
without manual sorting. Pulverized material
and rejects will be covered by hygienic
compost in a sanitary landfill. The tins
and ferrous metals will be separated and
baled, preventing fly attraction.
65-0328
Poole, N. D. Waste disposers. In Consumers
all--the yearbook of agriculture 1965.
Washington, U.S. Government Printing Office,
1965. p.141-143.
A grinder in the sink is essentially a small
metal cylinder or hopper with a motor to
operate a pulverizer; it shreds food wastes
and flushes them into the drain. In a
batch-feed disposer, one puts the wastes into
the hopper (one to two quart capacity), locks
the cover, turns on the water and the electric
switch. The food is then ground. In a double
switch arrangement, one is turned on by
locking the lid in position; the other is
turned on automatically as water reaches an
adequate flow. Neither starts the mechanism
without the other. The continuous-feed
disposer can be fed as it operates, but a
stray bone or spoon may slip inside,
accidentally. Soft dough, liquid fat, and
fibrous vegetables may require special handling.
Wastes from a grinder will increase the load
in a septic tank by one-third. The gas-fired
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0324-0332
incinerator consists of a heavy metal
container with a grate, a gas burner, and
an ash drawer built into the bottom. It
requires a connection to the fuel and to a
flue-fed chimney. Capacities range from 1.5
to 2 bushels. Afterburners consume smoke,
fly ash, and odors. Ashes must be emptied
often and non-burnable material removed from
the grate to prevent clogging.
65-0329
Refuse-reduction plant saves landfill space.
American City, 80(11):92-93 , Nov. 1965.
A new plant, just outside Montreal, can process
500 tons per dav, reduces bulk by 65 percent
(including salvage) and changes the nature
of the refuse. The refuse is collected by
20-ton compactors that discharge either into
the conveyor hoppers or into an adjacent
storage pit. There are three 8 hr or two
10 hr shifts. Seven trucks can dump at the
same time. A pan conveyor moves the refuse
from the hopper onto the conveyor belts which
carry it to a sorting room on the second
floor. Currently, metal, paper, rags, and
glass are salvaged and baled. Refuse weight
is reduced by 25 percent and bulk by 40
percent by the current operations. The
non-salvageable material passes to crushers.
Two hammermill units each have four 12-hammer
rows of 15 Ib swing hammers revolving at
1,200 rpm. All uncrushable material is
rejected ballistically. Costs are estimated
to be $1.50 to $2.00 per ton for operation or,
if capital is included, about $3.00 per ton.
One half will be recovered by salvage.
65-0330
Reno II. Public Cleansing, 55(10) : 564-566,
Oct. 1965.
The principle behind a new type of refuse
collection vehicle is explained. The Reno
II contains a 10-cu yd continuously rotating
drum with vanes which partially pulverize the
refuse and impell it towards the front of the
system, wets and compacts the refuse so
little cover is needed at the tip site.
Capacity of the truck is 400 bins in one load
of about 5 tons.
65-0331
'Seerdrum' refuse conversion plant. Engineer,
220(5731):897, Nov. 26, 1965.
The 'Seerdrum' refuse conversion plant at
Wheatley, Oxfordshire, is described. Domestic
rubbish is fed into the drum, which is 8 ft
in diameter and 29 ft long, and rotates at
11-- rpm. After 45 minutes the product and
rejects are disgorged. The product is a
broken-down, inoffensive material like young
leaf mould; the rejects comprise tins, rags,
plastics, and rubble. At the loading end a
metering pump introduces water into the charge
to bring its moisture content to about 40
percent. This moisture is instrumental in
reducing the strength of paper-based and
fibrous constituents to facilitate easy
breakdown during abrasion. The process is
described in detail and illustrations are
provided. Optimum capacity is 7' tons per
hr to 8 tons per hr and installed power 50
kW. Capital cost is much less than for
alternative methods.
650332
Shayne, P. E., E. H. Taylor, and K. S. Watson.
On-site development. In Proceedings; Technical
and Planning Aspects of Solid Wastes,
Columbus, Sept. 1965. Ohio Department of
Health. p.D-1 to D-27.
A recent invention is a self-contained refuse
compactor that compacts the refuse on site
and eliminates air pollution, daily collections,
extra personnel, and separation of refuse.
Six basic types of detachable containers in
the system are used. Containers are fire
proof, animal proof, rodent proof, fairly
free of flies and odors, and will hold more
than trash cans. The cleaning of containers
is a problem. The container itself can be
improved. A major problem is trained personnel.
Possible solutions to the problem include
incorporating these wastes into the sewage
system, and dissolving trash in acid. People
must be made aware of the long-range problem,
and must be educated in handling solid wastes.
Facilities to handle solid wastes must be
incorporated into new buildings, and financial
support must be given for long-range projects.
Advertising and public relations are proposed
to accomplish these. The sack system removes
the ontainer along with the contents. There
is no permanent container to attract insects
and other disease carriers. Odors, spillage,
and noise are greatly reduced. A food waste
disposer might be installed in each home and
the food waste problem combined with the
sewage problem. Slides were shown and the
operation and economics of the disposer
described.
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INCINERATION
65-0333
Angenend, F. J. The state of waste incineration
in the U.S.A. Brennstoff-Waerme-Kraft,
17(8) -.396-399, Aug. 1965.
This is a review of the 'Proceedings of the
1964 National Incinerator Conference,' ASME.
The individual topics of this publication are
briefly summarized. Some differences in
European conditions are noted, such as the
lack of interest in utilizing the heat
generated by waste incineration. The level
of the technology of waste incineration is
somewhat higher in Germany than in the United
States, but that much can be learned from the
American experiences. Waste incineration
needs more scientific research. (Text-German)
65-0334
Big incinerator nears completion. American
City, 80(4):21, Apr. 1965.
Rockville, Maryland, is building an incinerator
with three furnaces, each capable of burning
350 tons of refuse every 24 hr. The furnaces
feature the largest traveling-grate stokers
ever installed for a municipal plant.
65-0335
Bogue, M. D. Municipal incineration. U.S.
Public Health Service, Dec. 1965. 21 p.
A brief review is given of the history of
incineration, incinerator applications, a
comparison of incineration and sanitary
landfill, and the advantages and disadvantages
of incineration. The elements of an
incinerator system are the storage pit, the
furnace, the combustion chamber, the subsidence
chamber, a residue removal system, cranes,
and fly ash removal equipment. Some
incinerators will have forced draft fans and
air pollution control devices such as wet.
scrubbers or cyclone dust collectors. General
types of incinerators include: batch-feed
cylindrical and rectangular furnaces, and
continuous-feed furnaces such as rocking
grate, reciprocating grate, traveling grate,
rotary kiln, and ram feed. Factors which
should be considered when locating an
incinerator are: haul distance, central
location, zoning, waste heat market location,
clean water availability, expressway location,
truck access, land availability, land cost,
housing in immediate area, nuisance factors,
foundation conditions, exposure to floods,
availability of rail and water transportation.
Continuous operation of an incinerator may
save 15 percent or more in labor costs.
Recent advances in incineration and elements
requiring further study are listed.
65-0336
Boubel, R. W., G. E. Thornburgh, and B. R.
Pavelka. A study of wood waste disposal by
combustion and its effect on air quality in
the Medford Area/Final Report. Corvallis,
Oregon State University, School of Engineering,
Engineering Experiment Station, Jan. 1, 1965.
60 p.
A study was sponsored by the Forest Industries
Air Quality Committee of Associated Oregon
Industries to better understand the effects
of wood waste burning on atmospheric pollution
levels. The study was conducted in a small
valley area with a relatively large number
of teepee waste burners and relatively poor
quality air. Particulate emissions for the
area were estimated and air quality measured
for approximately 3 months. Teepee burners
were found to contribute the great majority
of particulate matter found in the atmosphere.
The air quality of the area was generally
unsatisfactory according to regulations of
the state of Oregon. Test results indicated
that the burners were capable of doing a
reasonable job of consuming wood wastes if
they were properly maintained and operated.
The critical period was during start-up when
low temperatures and correspondingly high
excess air occured with the resulting
excessive smoke and cinder discharge. The
best criteria for smokeless operation is that
the exit gas temperature be maintained within
the range of 600 F to 900 F. A cost analysis
for various disposal methods was made for
existing teepee burners; modified and refined
burners with temperature measuring devices;
auxiliary gas fuel, and full draft control;
multiple chamber incinerators with air
cleaning devices; and spreader stoker
electrical power generating stations. A
bibliography is appended.
65-0337
Brandt, H. Cleaning of flue gases.
Brennstoff-Waerme-Kraft, 17(4):190, Apr. 1965.
It is now possible to clean flue gases
escaping from waste incinerators. While older
incinerator plants annoyed the neighborhood
by discharging charred paper and cardboard
74
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0333-0341
flakes, the newest electro-filters retain
even the smallest particles of charred paper.
A new recording instrument, 'Konitest,'
indicates every change in the dust content of
the flue gases. (Text-German)
65-0338
Coogan, F. J., and J. H. Stovall. Incineration
of sludge from kraft pulp mill effluents.
Tappi, 48(6):94A-96A, June 1965.
The disposal of sludge from pulp and paper
mills has been a problem because of the land
requirements and the nuisance from unsightly
sludge ponds. The use of a sludge dewatering
system and incineration system for a bleached
kraft mill is described in which the total
waste from a 540 ton per day of bleached
board, coated and specialty papers facility
are disposed of in an area of a few hundred
square feet. The details, costs, and
operating problems of the plant are described.
The sludge was dewatered by passing through a
clarifier (1.9% solids in sludge), a centrifuge
(20% solids in cake) , and a filter press (36%
solids in cake). The filter press cake was
fluffed up before going to the waste heat
drier and cyclone where the solids were
increased to 77 percent before being charged
to the incinerator. A sketch is given of the
pilot plant flow diagram and the mill waste
treatment system showing the location of
the sludge incineration system. Tables are
given of the characteristics of the pilot
plant wastes, the pilot plant operating data,
and the operating costs of the incineration
system. The dewatering and incineration
system cost $158,000 and the cost of operation
was $12.48 per ton of dry solids incinerated.
The cost of operating the entire waste
treatment system was $0.40 per ton of
unfinished paper which was slightly higher
than the costs for sludge lagooning alone.
650339
Corey, R. C. Definitions of terms used in
incinerator technology. Informative Report
No. 1. Journal of the Air Pollution Control
Association, 15(3):125-1 26, 135, Mar. 1965.
The definitions given apply to conventional
commercial, industrial, and municipal waste
incineration practices. Typical of the
definitions is: Fly ash--all solids including
ash, charred paper, cinders, dust, soot, or
other partially incinerated matter carried out
in the products of combustion. The
classification system for incinerators and the
classification system for types of refuse
are those adopted by the Incinerator Institute
of America in the HA Incinerator Standards
of April 1963. The word waste refers to
useless, unused, unwanted, or discarded
materials including gases, liquids, and solids.
Refuse, as defined, refers to solid wastes,
such as garbage, rubbish, ashes, street refuse,
dead animals, abandoned vehicles, industrial
wastes, demolition wastes, construction wastes,
sewage solids, and hazardous and special
wastes. The classification of incinerators
includes the type of wastes for which each
incinerator class is suitable. For example,
Class VI Incinerators (crematory and
pathological incinerators) are suitable for
Type 4 wastes which are composed of human and
animal remains, consisting of carcasses,
organs, and solid organic wastes from
hospitals, laboratories, abbattoirs, animal
pounds, and similar sources consisting of up
to 85 percent moisture, 5 percent incombustible
solids and having a heating value of 1,000
Btu per Ib. This contrasts with Type I
waste, which is rubbish consisting primarily
of paper, cartons, rags, wood scraps, sawdust,
etc. consisting of up to 25 percent moisture,
up to 10 percent incombustible solids and
having a heating value of 6,500 Btu which can
be used in Class I, IA, II, HA, and II
incinerators.
65-0340
Easterlin, J. D. Complete combustion with
minimum excess air. American City,
80(2):99-101, Feb. 1965.
Broward County, Florida, has a new incinerator
which has two ram-fed furnaces. Detroit
stokers are built to a tandem design, charging
hoppers that can be loaded by crane or by
truck, stationary crane controls, and a
self-cleaning magnet that removes metal from
residue. Several patented improvements
include ash-removal and gas-scrubbing apparatus
and portions of the material-handling and
water-recovery system. The stack particulate
emission rate is well below Florida standards.
65-0341
Flood, L. P. Air pollution from
incinerators--causes and cures. Civil
Engineering, 35(12):44-48, Dec. 1965.
A detailed report on specific and common
causes of air pollution from incinerators and
design factors which eliminate these causes
is presented. The essentials are:
high-temperature burning in turbulent air
flow for sufficient time; use of 25 percent
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Incineration
more air than theoretically needed, and no
more; gentle, mechanical agitation of fuel
bed; cleaning of stack effluent by electrostatic
or other methods; high-stack to spread
pollution and help create a draft; continuous
feed to eliminate periodic excess air causing
smoking; water cooling to allow high
temperatures without slag formation; 3-shift
operation to eliminate smoking and incinerator
temperature-change stress at start-up and
shut-down. Drawings of European plants
following this formula are included.
65-0342
Gruenwald, A., and J. A. Reynolds. Less
than $3,000 per ton. American City,
80(10) -.100-101 , Oct. 1965.
Astute design and simple instrumentation
helped to hold the construction cost of the
new 250 ton per day incinerator in Ewing
Township, New Jersey, to less than $3,000 per
ton. The furnace itself contains a single
combustion chamber above the horizontal
traveling grate which rides on rollers to
minimize wear. Underfire air enters through
ten ports, double the ordinary number for
this length of grate, to provide more even
distribution and prevent blow holes. The
result is the lazy flame, so important to
air pollution control. Expansion changer
velocity totals only 1,000 ft per minute at
1,800 F. Performance indicates that with
this design no sprays are necessary in the
flues. Low velocities allow the particles
to precipitate in these chambers instead of
being forced out of the stack. The building
is constructed of concrete blocks framed in
Bethlehem steel beams. By knocking out one
sidewall, it will be possible to add another
unit and double the capacity if the future
should demand it. The design of the stoker
is described and because of the multiple,
closely spaced, air inlets, no auxiliary fuel
is necessary. Double furnace walls of
silicon-carbide brick extend 4 ft above the
stoker. An American Blower fan, with a
capacity of 34,000 cfm at 5 in. pressure,
supplies the air for combustion and
instrumentation is kept very simple. The
operation of the plant, which at present
employs only one shift, is described.
Operating cost is $2.50 per ton. If future
needs warrant, two or three shifts can be
used and a second furnace can easily be
installed.
650343
Halfgott, T., and P. Webber. Atomized
suspension technique incinerates sewage sludge.
Water Works and Wastes Engineering, 2(9):70-79,
Sept. 1965.
The Thermosonic Reactor System (formerly the
Atomized Suspension Technique) is an
incineration process for the oxidation of
sewage sludge to innocuous ash. After the
sludge is filtered, thickened, and ground, it
enters the top of the reactor as a mist and fine
particle spray. The sludge is atomized and
preheated, dried and evaporated, superheated,
and finally combustion occurs. The hot gases
of combustion flow up the annulus of the
reactor to help heat the incoming spray by
radiation through the annulus wall. The high
velocity of these gases carry out the dust
particles to a dust separator. Dried organic
compounds in the sludge are used as a fuel
supplement. The system is operated at a low
pressure, and there is no odor to the operation.
The percent of solids concentration in the
sludge greatly affects the performance of the
system. The viscosity of the sludge affects
the velocity of the system. The thickener
used in the system is a simple, moving fabric
screen that allows a flocculated sludge to
drain off water. Mathematical considerations
of effects which act upon the system are given
in this paper. Full scale operating data
should be available from the organization
using the system.
65-0344
The hazards of burning plastics. Public
Cleansing, 55(4):219-220, Apr. 1965.
The hazards of burning some plastics,
particularly chlorinated plastics such as
polyvinyl chloride (PVC) are discussed.
Chlorinated plastics give off hydrogen
chloride and carbon monoxide when burned,
both of which are poisonous, the former being
a pungent irritant, the latter odorless, and
both requiring special equipment to eliminate
them from incinerator exhaust. Chlorinated
plastics may be detected by the green color
imparted to a flame of a previously heated
copper wire when reheated with a trace of
the plastic. (Text-German)
65-0345
Incinerator fly ash meter under development.
American City 80(4) :21, Apr. 1965.
A monitoring device to measure particulate
matter in incinerator stack gases is under
development by the Illinois Institute of
Technology Research Institute, financed by a
grant from the American Public Works Association
Research Foundation.
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65-0346
Incinerator plant's closed circuit TV cuts
labor costs. Air Engineering, 7(7):20,
July 1965.
A municipal incinerator at Oyster Bay has
four closed circuit television cameras and
remote controls, which assist the operating
engineer by providing over-all plant
coordination and control.
sludge. A cvclone separates the solid
particles from the gases. Incineration of
sludge is necessary during the winter so as
not to overload the digesters. The operating
force consists of one man each for the filter,
drying, and bagging operation. Charts give
operating data and sludge drier performance
data for the period 1959 to 1964. This data
shows that the sludge drying process has
performed well, is reasonable in cost, and
is an important part of a public relations
program.
65-0347
Incinerators to cost Milwaukee $10 million.
Refuse Removal Journal, 8(3) :26, Mar. 1965.
Black & Veatch, a Kansas City, Missouri,
consulting firm, has recommended the
construction of two $5 million incinerators
to handle all refuse for the city of
Milwaukee. If the 11th largest municipality
in the United States accepts the findings,
it would have to purchase land from the
Federal Government. This report ruled
out the 1960 recommendation of one central
incinerator and sanitary landfill as an
alternative to incinerators, as no disposal
sites within convenient trucking distance
could be found. The new incinerators would
combine garbage and non-combustible material
to be collected and placed into the ovens
together. The two incinerators would have
three units each and be capable of disposing
1,800 tons of refuse daily. This capacity
could take care of a predicted population of
1 ,021,000 by 1985.
65-0348
Irving, C. E. Flash drying and incineration.
Water Works and Wastes Engineering, 2(9):70-72,
Sept. 1965.
The sludge drying facilities at Schenectady,
New York, have been in operation since
January, 1954. Equipment consists of three
vacuum filters, chemical equipment, and a
flash dryer equipped for drying, bagging the
product, incineration, deodorization, and
dust collection. The sludge, which comes
from a population of 80,000, is digested,
vacuum-dewatered, dried in a Raymond Flash
Dryer, and the resulting sludge is bagged.
The dried product, named 'Orgro' is sold for
$1.00 per bag. The filter cake is discharged
to the mixer where it is mixed with previously
dried sludge to reduce moisture content. The
cage mill does most of the drying by intermingling
the hot furnace gases with the conditioned
65-0349
Lieberg, 0. S. Heat recovery from
incinerators. Part 1. General considerations,
refuse handling, furnaces, waste heat
recovery, fly ash control, the heat balance.
Air Conditioning, Heating and Ventilating,
62(6):53-57, June 1965.
The present day design objectives for waste
heat incinerators include: a plant from which
the maximum benefit can be obtained from the
heat generated; to justify the cost of special
equipment to utilize the heat; and to burn
the refuse efficiently, economically, and
reduce it to a satisfactory residue. A
section drawing is given of the 750 ton per
day incinerator for the town of Hempstead,
New York. Also given is a table which shows
the hourly heat balance of an incinerator
having 20,000 Ib per hr charge of refuse with
a heating value of 4230 Btu per Ib. The
incinerator plant can be divided into three
sections: the handling of the refuse at
the site, discharge to storage bins, conveying
from storage bins to furnace, and the residue
removal; drying of wet waste prior to burning,
provision for burning the refuse, draft control,
auxiliary firing, stacks, etc., and fly ash
arresters, cyclone separators, settling
chambers or scrubbers. Incinerators for years
have had poor public relations and are
considered by the public to be associated
with smoke, sparks, offensive odors, and
being a general nuisance. However, the
control of air and water pollution which are
possible with careful planning, control, and
cooperation with public agencies should
eliminate the concern over public health and
nuisance problems. Despite the nearly 100
percent efficiency of electrostatic
precinitators, the control of air pollution
is best realized by thorough burning of
refuse which decreases the load on the fly
ash equipment. Only recently has waste
heat from incinerators been economically
applied.
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65-0350
Lieberg, 0. S. Heat recovery from
incinerators. Part 2. Generation of service
hot water and low, medium and high temperature
water for space and process heating. Air
Conditioning, Heating and Ventilating,
62(7):73-74, July 1965.
Heat recovery from incinerators for use in
hot water generation is discussed. Hot water
is required for many purposes in factories
and municipal buildings. In planning factories,
the incinerator building should be Located
adjacent to buildings where hot water is
required. For process work, where the demand
is sufficiently large, storage tanks can be
located within the factory near the heat-consuming
plant. A temperature range between 125 and
200 F can be easily controlled and a mean
temperature maintained, depending on the
requirements. An incinerator capacity of
500 tons of refuse day day will give an
output of heat, energy high enough to be
gainfully employed, either for steam raising
for turbo-generators or for heating of
buildings within piping distance. High or
medium temperature water systems with their
high heat 'thermal fly-wheel' reserve in the
pipelines are both economical and practical.
Several incinerator systems which generate
steam at 200 psig and temperatures up to 400
F are mentioned. The Oceanside, Long Island,
incineration pilant, which is probably the
first to use waste heat energy to provide
both electric power generation and
salt-to-fresh water conversion, is described.
Steam, which drives a 1,250-kw turbine generator,
is produced in two C.E. forced circulation
boilers each with a rated capacity of 85,000
lb steam per hr at 462 F and 460 psif,. A.
schematic representation of a heat recovery,
distribution, and utilization system for an
incinerator plant is presented.
65-0351
Michaels, A., C. A. Rogus, R. Novick, et al.
Incineration (Panel). In Proceedings;
Technical and Planning Aspects of Solid Wastes,
Columbus, Sept. 1965. Ohio Department of
Health. p.K-1 to K-42.
The main purpose of incineration is to get
rid of something. Various design
considerations are listed. The characteristics
of the refuse must be known. The major
chemical characteristic of refuse xvhich
determines the size of the units which form
the incinerator plant is its Btu value,
which may vary from 3,500 to 5,500 Btu per
lb. Grate loading requirements, air
requirements, the refractory problem, residue
handling systems, instrumentation, shift
operation, ventilation, and economics of
operation are discussed. The public health
aspect is becoming increasingly important.
Research and testing in the field is outlined.
An important consideration in the design of
the plant is the production of an effluent
acceptable from a health standpoint. The
effects of air pollution may be of an economic,
nuisance or health hazardous nature.
Estimated economic losses range from $60 to
$200 per person. Temporary effects include eye
irritation. Long term exposure to air pollution
has been ssociated with such chronic
respiratory diseases as asthma, bronchitis,
emphysema, and lung cancer. Increasing
attention has been given to the design and
operation of incinerators. Incineration must
achieve both maximum combustion efficiency
to reduce atmospheric discharge of smoke,
tars, malodorous compounds, and other products
of incomplete combustion; and maximum
retention of the incombustible solids. The
whole process of incineration tries to achieve
volume reduction, the residue ranging from
5 to 15 percent. The salvage or reuse of
residue is discussed. Questions directed to
the panel concerned: quenching water, a
rotary kiln type of incinerator, disposal of
sewage sludges and grass.
65-0352
Milton, H. E. Incinerator cuts air pollution
with new engineering devices. Refuse Removal
Journal, 8(6):22-23, 36, June 1965.
Stratford, Connecticut, has a new incinerator
with the latest design and equipment for high
combustion efficiency and air pollution control.
The incinerator is the pit and crane type
and has two 120-ton per day continuous feed
furnaces with a traveling grate. Municipal
collection of refuse is also described.
65-0353
Milwaukee must rush incinerators. Refuse
Removal Journal, 8(4):11, Apr. 1965.
Milwaukee has been looking for refuse dump
sites for the past 4 years without success.
William H. Rheinfrank, superintendent of
street sanitation said that the city's present
grounds could be used for another 2 years.
He urged that prompt action be taken on the
proposal for two new incinerators because
they take several years to build. Black &
Veatch, Kansas City, Missouri, consultants,
recommended that the city convert its present
refuse collection and disposal system, using
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0350-0356
two incinerators capable of burning all waste.
The incineration was necessary because
Milwaukee was running out of dump sites for
non-combustibles. The Finance Committee of
the Common Council has required the submission
of a detailed report outlining the procedures
necessary to put the Black & Veatch
recommendations into effect, which would
include cost data, information on traffic
patterns near the proposed incinerators,
and the possibility of building one central
unit. The incinerators will cost an estimated
$10 million.
65-0354
Montens, A. Incineration of waste oil and
oil sludges. Wasser und Abwasser,
106(14):382-383, Apr. 9, 1965.
The problems inherent in incineration are
basically the varying water content and the
impurities present in the waste oil and oil
sludges. The equipment used is discussed.
Filters must be used before the sludges reach
the incinerator, but the impurities may quickly
clog the filters. Low-viscosity waste oils
and oil-water mixtures are sprayed into the
flame chamber. Tar residues with a semi-liquid
or dough-like consistency are burned in a
revolving tube furnace; the tar is mixed with
sawdust so that it can be more easily deposited
in the furnace. Solid waste can also be
burned in a revolving tube furnace, which is
described and illustrated. Muffle furnaces
are suited for oil sludge incineration but
they are arranged horizontally so that the ash
is not discharged automatically from the
furnace, which fact is considered a great
disadvantage when this furnace is compared
with the revolving tube furnace. The turbulent
layer furnace is also used for the incineration
of oil and sludges although it cannot be used
when solid wastes are present. (Text-German)
65-0355
Moore, W. M. Teepee refuse burner has
extension dome. American City, 80(8):165,
Aug. 1965.
A tepee refuse burner for the incineration of
bulky wastes was put into operation in
January 1965 in Lexington, Kentucky. The Wilco
45 tepee refuse burner has the following
special features: (1) an extension, 20 ft
tall with a diameter of 16 ft 3 in., placed
atop the regular tepee model 45. Covered with
16 gauge hot-rolled Armco steel, the extension
lifts the dome to an overall height of about
70 ft. This permits more thorough burning
before the smoke escapes. (2) A special
concrete base for the burner, to support it
on the unstable landfill terrain. Supporting
this base is a 9 in. thick, reinforced concrete,
continuous core 'doughnut' with a 46 ft
outside diameter and a 40 ft 'doughnut' hole.
A 45 ft disk of reinforced concrete was
centered atop this footing, completing the
floor of the tepee. This slab was made 9 in.
thick around the rim, and from 14 in. to 30 in.
thick through its middle, with the thickest
portion at the center. Forced air feeds in
from underneath the floor slab through 7 in.
diameter pipes. Two iron grates, each 18 by
9 by 1 in., were used to make the 19 in.
square sets. These sets of grates were
centered on a radius of 7 ft 7/8 in, in the
concrete base, and are 9 ft apart on center
line. Total cost of installation was about
$15,500.
65-0356
National Research Council. Building Research
Advisory Board. Apartment House Incinerators
(Flue-Fed) Publication No. 1280. Washington,
National Academy of Sciences, 1965. 37 p.
The flue-fed incinerator can function
satisfactorily if it reduces the refuse to as
small a weight and volume as practicable without
discharging objectionable gases and pollutants,
acts as a temporary storage bin for refuse
without attracting or harboring rodents or
vermin, and remains simple to maintain and
operate, with most operations automatically
controlled. The three major air pollutants
resulting from incinerator combustion are
particulate matter, smoke, and odors. It is
recommended that no incinerator be permitted
to produce more than 0.85 Ib of particulate
matter per 1,000 Ib of any flue gas corrected
to 50 percent excess air. Design of new
incinerator installations should be placed
under the responsibility of an architect-engineer
firm having knowledge and experience in
combustion processes. For existing single-flue
incinerators, primary effort to improve
operation of the units should be directed
towards the combustion chamber, through
inclusion of adequate combustion equipment and
controls, controlled charging firing, and
automatic operations. For low-rise buildings
use of a single-flue incinerator with bypass
gas flue is acceptable provided that automatic
operation is utilized. Volume for single-chamber
incinerators may be calculated on the basis of
not less than 0.375 cu ft per person where the
burning period is 10 hr or less. Controlled
charging through the use of hopper door locks
and/or main flue gates should be employed. A
major coordinated program of research for
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incinerators and alternative methods of
apartment refuse disposal is recommended.
65-0357
Paltrier, C. L. Smokeless brush disposal.
Public Works, 96(51):90, May 1965.
Two smokeless brush burning plants of the
department of Public Works, Detroit, Michigan,
consume all tree trimmings, brush and logs
collected by city departments, and on a trial
basis, similar wastes from private nurseries
and landscapers. Before the construction of
the smokeless burning plants, the city disposed
of logs and brush by open burning, which
created local safety and air pollution
problems. An incinerator designed especially
for brush burning was developed. Built into
the incinerator are two burning chambers,
three wash chambers, a settling chamber and a
breeching (in that order). Two men are required
to operate each plant; one man operetes the
front end loader, the other directs traffic
in and out of the area, overseas the dunping
of loads and adjusts the forced air and wash
chamber water. Details are given as to the
structure and operation of the incinerator;
a diagram is included.
65-0358
Pneumatic conveyor speeds fly ash removal.
Public Works, 96(4):115, Apr. 1965.
A pneumatic ash conveyor system was placed
in operation at the municipal incinerator
serving Winnipeg, Manitoba, obviating the slow,
laborious removal of fly ash from settling
pits. The incinerator plant consists of
four manually stoked 100-ton Nichols Monohearth
furnaces of circular design and a newer,
200-ton capacity furnace equipped with Flynn
and F.mrich rocking grates with hydraulic
controls. Fly ash is removed once a week
from settling oits in the expansion chambers
leading to the chimney. A hose with intake
nozzle is attached to a pip in the Fuller
Airveyor/Airstream conveying system. The
system picks uo the ash and conveys it to a
receiver-filter outside the plant building.
Material collected in the receiver's hopper
is dropped into a waiting truck and hauled
away. Dust is trapped by cotton cloth bags
in the collector portion of the receiving
station, so no particles leave the system
to enter the surrounding plant atmosphere.
By comparison with former methods, the
pneumatic conveying system has greatly
reduced the manhours required for this weekly
cleaning task. However, the real saving is in
furnace burning time. By doing the job more
quickly the five furnaces can be put into
operation 2 hours sooner than by the previous
method of cleaning. At the rate of 25 tons
per hr, this enables the plant to handle 50
tons more refuse per week.
65-0359
Guillen, D. Low cost refuse burner eliminates
dump. Public Works, 96(3):96-97, Mar. 1965.
Dodge City, Kansas, uses 'Burn-0-^atic' refuse
burner, of conical shaped steel having a
forced draft system. Centrifugal blowers
supply underfire air through underground
piping. The dome is screened to allow
combustion gases to escape and to retain
burned particles such as paper ash. Total
height to the top of the dome is 57 ft 6 in.
The rated capacity of the burner is 7,500 Ib
per hr. The present refuse disposal requirement
is to handle 140 tons per week. Refuse is
discharged on the floor of the receiving
building from which it is pushed onto the
conveyor belt by a front-end loader. The
burner is operated from 9 am to 4 pm, being
started merely by firing some dry material
within the enclosure. The entire cost was
$52,000.
65-0360
Refuse disposal and open burning. In A
compilation of air pollutant emission factors
for combustion processes, gasoline evaporation,
and selected industrial processes. Cincinnati,
U.S. Public Health Service, May 1965. p.31-35.
The source emission factors were compiled
primarily for use in conducting an air
pollutant emission inventory. The compilation
is the result of an extensive literature
survey. A brief description and the emission
factors for the common types of municipal,
industrial, commercial apartment, and
domestic incinerators are given. Open
burning, whether in dumps or in very simple
backyard contrivances, gives rise to
emissions that are extremely variable and
difficult to measure. The data for backyard
burning were derived from tests on burning
mixture of 50 percent newspapers and 50
percent grass clippings. Factors for burning
dumps and for backyard burning are listed.
The emission of particulates from the
uncontrolled burning of automobile bodies
would be about 10 Ib of particulates per
automobile burned.
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65-0361
Refuse furnace to desalt water. Engineering
News Record, 175(8) -.23-27, Aug. 19, 1965.
A system in which refuse is used as fuel for
desalting ocean water in the $6-million
Oceanside Refuse Disposal Plant, is described
and illustrated. Hot gases from the furnaces
generate steam in boilers. The steam is first
used in the turbine generators, then circulated
through a closed system (four single-stage
submerged-tube evaporators) where it is
cooled with salt water pumped from a nearby
salt-water inlet channel. The heat transferred
in the evaporators boils the salt water to
steam. Steam is drawn off and condensed to
fresh water and the concentrated brine is
pumped back to the inlet channel. Fresh water
is stored in a 500,000 gal underground storage
tank for use in the plant as boiler make-up,
cooling, and flyash removal sprays. It is not
used for drinking purposes. The air pollution
control used in this system is briefly
described. It is estimated that a
high-efficiency combined refuse-disposal-desalting
plant, with a capacity to burn 1,000 tons of
refuse each 24 hr, could produce between 12
million and 14 million gal of fresh water a
day at a cost of $0.45 per 1,000 gal of water.
650362
Rehm, F. R. Test methods for determining
emission characteristics of incinerators.
Informative Report No. 2. Journal of the Air
Pollution Control Association, 15(3):127-135 ,
Mar. 1965.
Standardized test methods for determining air
pollution characteristics are important because
any standardized emission limitations would
be worthless without standard test methods.
This report of the Air Pollution Control
Association's TA-3 Incinerator Committee
represents the 'best thinking' of the
Association on incinerator emission testing.
The report if limited to the discharges of
greatest immediate concern: visual emissions
(smoke), particulates, and odor. Although
the Ringelmann chart leaves much to be desired
in efforts to assess the visual or smoke
emissions, it is basic in the field of air
pollution control and, until a better tool
evolves, it will be the most frequently used
method of assessing visual smoke emissions
from incinerators and all other combustion
processes. In the domestic gas incinerator
field the Batelle CO method appears to have
merit. It is based on a demonstration that
the CO content is a valid indicator of the
odor intensity with gas incinerators using
a standard waste. For other incinerators, the
ASTM Standard D1391-57 may be acceptable.
The method is based on the dilution with
odor-free air until the odor can just be
perceived. For particulate determination,
there has been much research, but it is believed
that the ASME Test Code PTC 21-1941 and PTC
27-1957, with modifications and additions,
could be the basis of a standardized test
method for determining incinerator particulate
emission characteristics in spite of the
differences with WP-50 Bulletin of the
Western Precipitation Corporation. This
article reports the progress toward standardized
test methods rather than the methods.
650363
Rogus, C. A. Incineration. In Proceedings;
Technical and Planning Aspects of Solid Wastes,
Columbus, Sept. 1965. Ohio Department of
Health. p.J-3 to J-12.
The disposal of municipal solid wastes in
the large community has favored incineration
due to the difficulty of obtaining adequate
and suitable land for sanitary landfills, the
increasing per capita output of refuse, and
the increasing calorific value of refuse.
Mechanization and automation have stimulated
modern incineration. Central incinerators burn
refuse at high temperatures and reduce the
combustibles to an inert, organic-free residue
which can be disposed of by landfilling.
Incinerators may be of the 'batch' type which
operate with intermittent charging of refuse
and discharge of residue, thereby creating
non-uniformity in burning temperatures. This
stirs up fine dust and subjects the refractories
to shock temperatures, and for these reasons
the batch type furnace is going into disfavor.
The 'continuous' type furnace and incinerator
overcome these shortcomings and are more
economical to operate. The major components
of the modern plant, which are described, are:
tipping floors, storage pit, cranes, furnaces,
residue system, combustion chambers, subsidence
chambers, and chimneys. Incineration is
prompt, health hazards, and odors are destroyed
or alleviated and costly collections are
dispensed with. The major disadvantages of
incineration are: the higher costs of
construction, generally higher costs of
operation and maintenance, the greater skills
required for efficient, nuisance-free operation,
and the need for final disposal of the residue
by landfilling. The historical background,
basic design considerations, and construction
and operating costs of incinerators are
discussed. In determining the design
capacity of an incinerator, seven major items
must be considered: the plant's objective,
type of refuse to be processed, amortized
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life, number of plants, daily and seasonal
variations in refuse output, operating shifts.
and plant operating factor.
65-0364
Sager, J. C. Scum disposal bv incineration
at the Minneapolis-Saint Paul Sanitar^-
District. Journal of the Water Pollution
Control Federation, 37(9):1243-1246, <=ept. 1965.
The development of the Minneanolis-St. Paul
scum incineration system fron a pilot sewage
treatment riant which is the first of its
type in the United States is described. A
line sketch of the system shows the troughs
into which the scum from the primary tanks
is skimmed by hand, the disintegrator in
which twigs and corks are broken up, the
decanting tanks and the feeder tank which leads
to the incinerator. The sketch includes the
design of the incinerator, which has no moving
feed equipment or grates. The decanted scum
is pumped into tue top of the primary ciamber
and falls onto a slightly sloping brick hearth
and onto downstepped cast iron tuyers, with
most of the active burning taking place in
the prinarv chamber. The gases eo over a
baffle wall irto a secondary chamber and then
through a latticed or perforated brick wall
into a short chamber before going to the
breeching and stack. The four oil burners
are located in both the prinarv and the
secondary combustion chambers and are
automatically controlled. The burners use
No. 2 oil and cut out at 1,600 F. The
ouantitv o*~ ash removed daily amounts to a
few nails. The svstem has worked well with
little maintenance and no smoke or odors.
During 1963, 1,612 tons of decanted scum were
incinerated in 274 days. The scum had an
average of 9,280 Btu per Ih with 62.8 percent
solids. The average amount of scum incinerated
per day was 5.9 tons, with 14.5 gal of No. 2
oil per ton of scum. Previous problems with
disposal of sewage scum have been eliminated.
65-0365
Sewage sludge incineration.
Chemie-Tngenieur-Technik, 37(5):556, May 1965.
A higb- temperature, low-pressure method has
been developed by the Pulp and ^aner Institute
of Canada for the incineration of sewage sludge.
The sludge is partly dehvdrated and pumped
into the reactor, which is made of stainless
steel and insulated with firebricks. At the
upper end the sludge is atomized with the
aid of a nozzle; at the bottom hot air enters
at high speed. The pressure in the reactor
is very low (apnrox. 76 cm water column) so
that the water vaporizes. The rapidly dried
particles are either gasified or burnt. The
waste gases nass through a heat exchanger to
regain part of the outgoing heat to preheat
the reactor air. The waste gases are freed
from the dust in a centrifugal separator and
escape through a chimney. To prevent odors
the temperatures in the reactor must he
constantly kept between 760 and 1,100 C.
(Text-Cerman)
650366
Smokeless brush burning plants reduce air
pollution in Detroit. Refuse Removal Journal,
8(3):8-9, 30, Mar. 1965.
Two smokeless brush burning plants in Detroit
have eliminated open burning. The Department
of Parks and Recreation is the major user of
the plants which burn tree trimmings, brushes,
and logs. Each plant features a 44-ft-long
furnace. qmoke, fly ash, and other particles
are tranred by a series of wash chambers.
The plants are well under Detroit's minimum
pollution control requirements.
650367
Speer, R. D. A crematory for animal disposal.
American City. 80(8):121-122 , Aug. 1965.
A special small animal crematory is
incorporated into the new Hartsfitld incinerator
in Atlanta, Georgia. The crematory has a
total capacity of 1,000 Ib per hr after the
furnace reaches burning temperature. Trucks
dump directly onto the two charging chutes on
the floor directly above the furnace. The
natural-gas fuel contains 1,040 Btu per cu ft,
and its specific gravity is 0.6. Five burners,
of the blast t\pe, with electric ignition and
starters equipped with automatic flame-failure
controls, operate this foolproof system. The
three burners in the primary (loading) chamber
area 'nave a total capacity of 5 m Btu per hr.
In the secondary chamber two burners with a
capacity of 3 m Btu per hr burn all gases,
thus eliminating odors completely. The
insulation-lined breeching between the furnace
and stack is brick. A guillotine-type damper
at the beginning of the breeching and a
flue-gas scrubber, for flv-ash removal,
located at the end near the stack intake,
comnlete the furnace layout. The animals are
consumed completely and only calcified bone
ashes remain which are used to fertilize the
incinerator grounds. Refrigeration of the
animal corpses allows the burning to be
concentrated into 2 days per week. This has
added to the economy of the system.
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65-0368
Sterling, M. Brush and trunk burning plant
in the City of Detroit. Journal of the Air
Pollution Control Association, 15(12) :580-582 ,
Dec. 1965.
Air pollution laws have been difficult to
enforce in Detroit because of burning of
Dutch Elm-diseased trees, brush, and trunks.
Strict compliance with ordinance requirements
prohibiting open burning by house wreckers,
scrap reclaimers, and landscapers was
difficult. A sketch is given of a brush
burning incinerator showing the charging door
for bru,sh at one end and the log charging
door at the other end. The combustion gases
pass a water spray system before discharge
from the 6-ft diameter, 150-ft high stack.
The results of stack sampling tests are given
in a table which shows the gaseous and
particulate emissions from the incinerator.
An average of 1,000 cu yd of brush and trunks
are charged in an 8 hr shift. The primary
chamber for brush is equipped with a 12 by 10-ft
horizontal sliding, motor operated charging
door operated by radio control from the cab
of a front-end loader. This allows the
operator to charge the brush without leaving
the vehicle cab. The secondary or log-burning
chamber is similarly equipped. The reduced
Detroit particulate emission limitations of
0.09 grains per cu ft at 500 F at 50 percent
excess air are well above the emission
determined. The ash, amounting to 5 cu yd a
week and representing a 99.9 percent volume
reduction is removed after the unit cools over
the weekend. Because of the success of this
plant, another one is being constructed to
take care of all brush and trunk wastes.
With extra underfire air admitted toward the
rear of the primary brush chamber, a wider
variety of wastes, such as Christmas tree,
can be handled. The city of Detroit now
complies with its own air pollution ordinances,
and the burning plant should interest other
cities.
When tipped, the pulverized material is not
attractive to vermins as it is an almost
odorless paste-like material. It heats
readily to 165 F commencing to compost almost
at once. It can now be shown costs can be
reduced and handling capacity increased. When
grinding food at the source, the grinder is
below the sink and attached to an outlet.
Cold water flushes residue out of the grinder
and into the sewer. Its value is in health
and hygiene. Several cities in the United
States have large central grinding depots to
deal with separately collected garbage too wet
to incinerate.
65-0370
TV to monitor incinerator operation. American
City, 80(1):34, Jan. 1965.
In Oyster Bay, New York, four television
cameras will assist the operation of an
incinerator. The plant, scheduled to start
operating in the fall of 1965, will have two
cameras on the charging floor to survey the
entire bin area. Each of the two furnaces
also contains a camera focused on the burning
grate. Two monitors are located on a control
console in the operating engineer's control
room, where the operating engineer can view
either the furnaces or the bin. This
closed-circuit television system eliminates
the need for constant supervision of additional
men, and results in closer control over the
burning capability of the plant. On the
furnace monitors, the operating engineer can
detect whether it is necessary to increase
or decrease grate speed to achieve optimum
operating conditions. The controls for varying
the amount of overfire and underfire air
water spray, for example, are mounted near the
monitors, 1,200 units of industrial television
are utilized across the country in similar
utility plants.
650369
Stirrup, F. L. Pulverization and grinding.
In Public Cleansing; refuse disposal. Oxford,
The Institute of Public Cleansing, 1965. p.59-71.
Pulverization is used to reduce volume. Refuse
is fed in the top of the pulverizer, struck
by rotating hammers and shredded. It must be
sufficiently small to pass through screen
bars. Preseparation of materials likely to
cause damage is essential. Metal objects are
discharged into a separate chute and subsequently
sold as clean metal. Material is separated
into dust, pulverized refuse, and rejects.
65-0371
Wangerin, D. D. Waste-heat boilers...principles
and applications. Combustion, 37(3):24-31,
Sept. 1965.
In spite of the inducements to use 'free' fuel
such as is provided by bark and wood refuse,
black liquor, municipal and industrial wastes,
and sludges, wastes are extremely poor fuels
compared to the usual prime fuels. A table
shows that the prime fuels are three to four
times more effective than waste fuels.
Another table shows that the waste fuels
have high moisture and often high ash content.
The problems encountered by the boiler
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Incineration—Eui ope
designer in developing special equipment to
utilize the meager heat content of these fuels
are described. The discussion is limited to
the utilization of the principal waste products
available in the pulp and paper, steel, and
petroleum industries. The designer must
tailor his unit to meet the worst possible
conditions witn the major attention directed
toward fuel-burning equipment with adequate
combustion air to obtain maximum efficiency
and minimum carryover. Large furnaces to
complete combustion and absorb sufficient
heat before the gases enter the convection
area, and low gas velocities and widely-spaced
convection surfaces to prevent plugging and
erosion are necessary. Line drawings are
given of a 1,000-ton black liquor recovery
unit, and three drawings of bark boilers,
including provision for auxiliary coal of
natural gas. Six illustrations covering the
combustion of waste gas from the steel industry
are included. There are many waste products
from which heat energy can be recovered, but
each has characteristics that require a
boiler of special design. Multiple-fuel-fired
boilers can dispose of waste products while
minimizing the cost of prime fuels.
65-0372
Weller, L. W. Pipeline transport and
incineration. Water Works and Waste Engineering,
2(9) -.66-69, Sept. 1965.
In Kansas City, Missouri, economic and location
factors favor the use of a single sludge
processing plant where raw sewage sludge will
be pumped a distance of 35,000 ft between plants.
The 12-in. diameter pipe has no bends greater
than 22'-< degrees and the 1 percent maximum
solids concentration liquid will flow at the
rate of 1 ,000 gpm. Two pumps in parallel with
a force main 'C' value of 100 will operate
continuously. Facilities for cleaning the
sludge pump piping include a cleaning tool of
'pig' which would be lowered into the pump
discharge line and forced through the valves
into the line. Also steam injection methods
have been provided for cleaning. Removal of
the 'pig' is relatively simple, effected by
moving it through by-pass valves so that the
flow is not hindered. Chlorine can be injected
into the pipeline to control slime growth and
odor by means of a chlorinator equipped with
a flow recorder and integrator. The pipeline
is easily accessible by a series of manholes.
The sludge will be discharged from the force
main into a thickener; it then goes to a
continuous belt cloth type vacuum filter for
dewatering processes. Finally the filter
cake produced is ignited.
65-0373
Winkler, T. E. Incinerator serves suburban
communities. Public Works, 96(12):74-77 ,
Dec. 1965.
The incinerator for Central Wayne County,
located in Dearborn Heights, Michigan, began
operation in 1964. It provides for minimum
hau]ing costs for five surrounding communities.
Having an ultimate capacity of 750 tons per 24
hrs, the plant is of the crane and bin type
with continuous feed, reciprocating grate
stokers. Two furnaces are now installed, each
with 250 ton capacity. Ashes are quenched
and discharged into a truck for removal to a
landfill. Total cost of the incinerator,
including land and engineering was $2,368,000.
Operating costs are estimated at $4.50 to
$4.75 a ton of refuse processed.
INCINERATION-Europe
65-0374
Bradford's new refuse disposal plant.
Surveyor and Municipal Engineer,
125(3793):39-40, Feb. 13, 1965.
The new incineration and separation
plant built at the cost of fc430,000
which was made necessary because of a
shortage of tipping space is described.
This new incinerator created more than
usual interest because the tipping
operation at Bradford was well-known
and attracted many visitors and men
for training for fifty years. A
picture showing a general view of the
plant also shows the 180-ft chimney.
The other pictures show the
hydraulically-operated carcass and trade
waste charging doors on the tipping
floor, a general view of the salvage
room showing the sorting belt and the
overband magnetic separator, and the
top charging floor of the incinerator
with a reversible shuttle conveyor which
feeds the tailings to the charging door.
Large areas of glass give natural light and
good working conditions with special
attention being given to internal
finishes to ease cleaning and maintenance
chores. After weighing, the trucks enter
the reception hall and deposit their
loads into 100 cu yd hoppers, the base
of which is a slow conveyor. The conveyor
feeds to the primary revolving screen to
remove most of the dust before the
picking conveyor, which feeds to the
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0372-0379
secondary screen with dust and cinders
going to the cinder hoppers. The
incinerator is of the 5-cell Heenan
mechanical type with an additional cell
for trade wastes or bulky material. The
quenched clinker from the incinerator is
discharged to a skip for deposit in a
loading hopper for trucks.
incineration of plaster castings, kitchen
wastes, disposable bed sheets, animal
carcasses, tissues, etc. Prior to
loading, the furnaces are heated up to
the operating temperature by an oil or gas
burner. To avoid odors the waste gases
are led through an afterburner. (Text-
German)
65-0374
Built for growth.
55(2):81-84, Feb.
Public Cleansing,
1965.
Kidderminster, England, with present
population of 43,000, has opened a
separation and incineration plant, which
can later be expanded with two extra
incinerator cells to serve 70,000 people.
Landfill space for the next 5 years would
have cost $200,000. A brief description
of the operation from conveyor belt sorting
to incineration in the 4 semi-mechanical,
trough grate units is included.
65-0376
Continuous grate for the new Birmingham
plant. Public Cleansing, 55(10):588-589,
Oct. 1965.
Birmingham, England, is to be served with
a continuous grate incinerator, which will
operate in sections, with mechanical
fingers moving the refuse along the grate,
and each section having separate controls
and air supply. Because of expense,
pulverization wasn't to be used unless
necessary. Large items would be incinerated
separately. Tin cans were to be
incinerated and not recovered.
65-0377
Exhibit for hospital equipment in
Dortmund between May 19 and 22, 1965.
Staedtehygiene, 16(5) :125, May 1965.
At the exhibit for hospital equipment the
company Ruppmann, Stuttgart, West Germany,
showed 3 types of waste incineration for
hospitals; one with a capacity of
approximately 0.2 cu m per hr, one with
approximately 0.75 cu m per hr, and one
for 0.5 cu m per hr. The latter one can
be used for incineration of standard
hospital waste as well as for moist trash
from the operating room. It has a
furnace substructure for dustfree waste
removal. The furnaces permit a sanitary
65-0378
Fairlie, P. D. Correspondence. Public
Cleansing, 55(3):175-176, Mar. 1965.
Several aspects of mechanical vs. static
grates and power utilization in incinerators
are discussed. Mechanical grates were
felt to provide higher burning rates, but
all factors had to be considered. Some
British cities requested bids for both
static and mechanical wastes in their
proposed incinerators. Heat utilization
for power and steam was felt to be
economically impractical, because of the
somewhat undependable nature of the fuel
and fuel supply, which would necessitate
an expensive reserve power plant.
650379
Fairlie, P. D. Incineration plants
without heat recuperation. Public
Cleansing, 55(6):356-377, June 1965.
Arguments for incineration of refuse
without recuperation of heat for steam
or electric power, and the general types
and operation of incinerators and
associated equipment are discussed. The
640 ton per day Govan, Scotland incineration
works were designed in 1928 for electric
power production, and produced 40 million
kwh in 1936 with a revenue of $90,000 but
only 8J-2 million kwh in 1945 with a revenue
of $18,000. The Govan works are now
reconverted to incinerate without heat
utilization. Special emphasis is placed
on experience and operation of all phases
of the Scottish works at Govan and Polmadie,
and diagrams and thorough explanation of
these 800 ton per day, two-shift plants are
included. The rate of burning on mechanical
and static grates is discussed. Various
methods of charging and clinkering the
cells are explained. Dust collecting
equipment is reviewed regarding standards,
efficiency, and cost. Working data and
examples of dry mechanical, electrostatic
precipitators, and wet dust collectors are
shown. Separate incineration of bulky and
trade refuse with utilization of heat
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Incineration—Europe
for plant use Is handled. The design and
operation of the salvage section is
explained with criteria for selection of
conveyors, and types of atmospheric dust
cleaners for the plant. The overall cost
of disposal at these two works is about
$3 per ton including $1 per ton load
charges based on a 30 year life.
65-0380
Flue, dust extraction systems. Public
Cleansing, 55(7):434, July 1965.
Comments on Schieble and Multi-vortex
flue dust extraction systems, both of
which are operated in Glasgow incinerators
are given. The Multi-vortex plant used
with a water trough at the chimney base
collected 30 Ib per ton burned which the
Schieble plant collected 36 Ib per ton
but needed a heat exchange to avoid white
chimney smoke.
65-0381
Gross, A. T. Common incineration of
sewage sludge and trash. Brennstoff-
Waerme-Kraft, 17(11):562-564, Nov. 1965.
The common incineration of sewage sludge
and waste was the main theme of discussion
at the annual meeting of the association
for waste water technology held in Frankfurt
from September 28 to October 2, 1965. The
highlights of the discussion are reported.
Sewage sludge from settling tanks can be
reduced to 1/4 of its volume through
rotting. It is at the same time the most
economical method for dehydrating the sludge.
The sludge from biological plants can
only be reduced to half of its volume.
There are three possibilities for treating
sludge and waste in common. The common
dumping is of no great advantage mainly
because of lack of disposal sites. A
common composting, however, can be taken
into consideration especially so because
the completely sterile end product can be
deposited everywhere, should there be no
possibility of selling it. With the common
incineration the sludge must be dried first
to raise its heating value to that of the
trash. The heat from the trash is usually
sufficient for drying the sludge. From the
various methods of incineration the
Ebinger method must be mentioned. Here the
trash is added to the drying sludge in a
story furnace. Of disadvantage is the
necessity to crush the waste first. When
comparing the two methods, common
incineration and composting, with each
other to assess the advantage of one over
the other, one must first answer the
questions, how much residue remains, and
what is the cost per ton of waste? The
first question is answered in favor of
common incineration. Almost half as much
residues are left from incineration than
from the combined process of composting
and incinerating. Comparing costs,
composting is favorable. If the sale of
compost or slag is not considered, the
price relation is 27 DM per ton for
composting vs. 38 CM per n for incineration.
(Text-German)
65-0382
Incineration of bulky materials. Public
Cleansing, 55(7):399-403, July 1965.
The trend towards separate incinerators
for large, bulky and hard to dispose of
materials in Britain is explained. Most
cities now have provisions for incinerating
dumped household furniture, parking boxes,
and other items regardless of regular
disposal methods.
65-0383
Incinerator furnace capacity 2.84 cu.
ft. Engineering, 199 (5164):473, Apr.
9, 1965.
Stated to provide a quick and hygienic
means of disposing of waste, the Junior
incinerator is made by Maywick Appliances
Limited, of Wickford. The unit is
obtainable for operation on solid fuel,
propane, or town gas; heat input of both
gas-fired models is 105,800 Btu per hr. In
the case of the propane-fired model, the
gas rate is 41.5 cu ft per hr; that of the
unit using town gas is 210 cu ft per hr.
Furnace capacity is 2.84 cu ft. The
height of the unit, without the flue, is
2 ft 8 3/4 in.; the length of the flue
pipe, which has an outside diameter of
&% in., is 8 ft 6 in. The incinerator
measures 1 ft 61-$ in. wide and has a
depth of 1 ft 8% in. The loading door is
1 ft 6 in. by 1 ft. The weight is
approximately 5 cwt. The incinerator is
supplied ready for use; a galvanized
chimney with cone cap, and a steel rake
for ash removal are included. Among the
optional equipment which is obtainable
are: an after-burner, with flame failure
device; a main burner flame failure device;
a time clock controlling the main burner;
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0380-0386
and a lighting torch. Where the matter
to be disposed of is waste with a high
water content, or animal matter with a
low fat content, operation on coke is
reported to be particularly economical.
Tested on a poultry farm, it was found
that the incinerator would consume 80
Ib of diseased birds using only 5 Ib of
propane and a small bed of coke, for a
total cost of 4s.
65-0384
Incinerator specifications. Waste Trade
World, 106(5):8, Jan. 30, 1965.
The requirements for incinerators for
waste are indicated in a description of
the specifications of a recent standard
published by the British Standards
Institution. The latter is concerned
with waste from trade and residential
premises and capacities between 50 and
1,000 Ib per hr. The rating of
an incinerator (capacity in cu ft and
burning rate in Ib per hr) are related to the
weight, nature, and bulk density
of the refuse. The capacity and burning
rate of an incinerator, therefore, should
include the characteristics on which the
rating is based. The grate construction
should be of such size as to accommodate
the specified burning rate. For materials
with a high moisture content, an incinerator
in the range covered by specification should
be capable of being equipped with a
hearth and ancillary burners. The
volume of the burning chamber should be
adequate to enable the refuse to be burned
at the specified rate. The specifications
cover furnace lining, surface temperature
features, access doors, external finish
of the outer casing, charging door size,
ashpit design, agitator, provision of
air for primary and secondary combustion,
and supplementary heating for primary
combustion. Consideration is given to
safety factors, smoke emission, and flue
size. Notes are given on suitable
categories of waste and the Clean Air Act
of 1965; installation and operation are
given in the appendices. A list is given
of types of wastes not within the scope
of the specification, such as rubber,
plastics, wood, scraps, paints, animal
carcasses, remains, or sludges which
require special installations designed for
the specific purpose.
65-0385
Ingwersen, H. H. Experiences with a
novel waste incinerator grate.
Staedtehygiene, 16(10) -.223-228, Oct. 1965.
The roller grate, 'System Duesseldorf', was
developed especially for waste incineration
by the two boiler manufacturers
Durrwerke AG, Ratingen, and Vereinigte
Kesselwerke AG, Duesseldorf, in
cooperation with the department of
utilities of the city of Duesseldorf.
Today, ten plants equipped with this
grate are either planned or in operation.
Their characteristics are summarized in a
table. The grate consists of several
rollers of 1.5 m diameter. Each roller is
driven individually by gears and the
speed can be varied from 0.4 to 8
revolutions per hr. Because of this low
speed the waste burns uniformly and very
little (1 to 6 g per cu m) dust develops.
Temperatures between 900 C and 1000 C
ensure a flue-gas free of odors. These
limits are maintained by additional oil
or gas burners, or respectively by high
excess air supply. Experiences with the
incinerator in Rosenheim, Bavaria, are
reported in detail. Relevant data are
summarized in a table. The incinerator
uses 4.5 tons of waste per hr in continuous
operation from Monday through Friday. It
produces 7.5 tons per hr steam at 12
atmospheres which is fed into the municipal
remote heating system. Overall-efficiency is
65 percent. The plant in Rosenheim cost
2.8 million DM which will not be recovered
by the sale of heat. (Text-German)
65-0386
Kachulle, C. Waste incinerators with and
without using the heat. Brennstoff-Waerme-
Kraft, 17(8):391-395, Aug. 1965.
The third congress of the International
Work Group for Waste Research (IAM) took
place in Trento, Italy, from May 24 to
29, 1965; 650 scientists and experts
from Europe, the United States and the
Near East participated. The main theme
was waste incineration with and without
using the heat. Four papers presented
are reviewed. H. Rousseau, France,
described incinerators in and around
Paris. He presented a detailed cost
analysis for the incinerator
Issy-les-Moulineaux, which cost 100
million francs and has a capacity of
68 tons of waste per hr. With using the
heat for electric power, the plant can be
written off in nine years. P. D. Fairlie,
Glasgow, said that in Great Britain heat
from waste costs about twice as much as
from conventional fuel and that, therefore,
waste incinerators usually do not utilize
their heat. In Glasgow, waste with a
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Incineration-Europe
grain size below m in. is not incinerated
but used as mulch, The paper by C.
Kachulle which describes the waste
incinerator to be built near Cologne
at Goldenbergwerk, is reviewed in detail.
It will incinerate 1.3 million tons per year.
The net deficit will be 10 to 17 DM per ton.
Schematics of the over-all design and the
Weyrauch-Babcock boiler are given. The
plant will serve a population of 4.I
million, will cost 40 to 50 million DM,
and will sell its heat to electric power
plants. The paper by K. Schwarz emphasizes
the advantage of large incinerators over
small facilities, in particular with respect
to air pollution problems. (Text-German)
65-0387
Kampschulte, J. Elimination of household
and bulky waste as well as of special waste
in Hamburg. Staedtehygiene, 16(10):218-223,
Oct. 1965.
In the year 1964, Hamburg had an accumulation
of waste of 2.5 million cu m, of which 1.08
million cu m could be burned while the
remaining 1.42 million cu m had to be
dumped. A new incinerator plant is
presently under construction at the site
of an already operating waste incinerator.
In the new plant, wastes from freighters
and passenger boats (mainly packing
material), bulky waste from households and
industries will be crused and burned. Oily
sludge will be added to the waste for
incineration. The new plant has been
designed for a capacity of 12 tons per hr
at a maximum gross heat capacity of 23 G
cal per hr. The steam boiler has been
designed for a maximum capacity of 27
tons of steam per hr. A layout of the
incinerator plant together with the newly
planned buildings is given. Cranes bring
the waste to a loading funnel through which
it falls onto the grate. The grate spans
a surface of approximately 31 sq m. It is
4 m wide and has 15 poking stages. Nozzles
distributed across the width of the grate
spray the oily waste into the combustion
chamber. The slag is treated for further
utilization. The hot slag gases are led
to an electro-filter from where they escape
through the slag gas duct and the
chimney (80 m high) into the air. The
waste from the harbor is brought in barges
on the canal to the incinerator plant.
It is planned to use 3 and 5 cu m containers
for the transport. A Hazemag crusher of
small capacity, which has been set up
experimentally several years ago, serves
for crushing the bulky waste and the slag.
A crane brings the waste from the barges
to the crusher. If the waste is brought
on trucks they tilt the load into a
bucket (volume 15 cu m) which is lifted
and emptied into the crusher. The
crushed waste falls onto a conveyer belt
bringing it to the storage room. A
diagram and a photograph illustrate the
Hazemag crusher. (Text-German)
65-0388
Knoll, H. The waste incinerator plant of
the city of Nurnberg. Brennstoff-Waerme-
Kraft, 17(12):595, Dec. 1965.
The waste incinerator plant in Nurnberg
will go into operation in the fall of
1968. Two furnaces will burn 300 to a
maximum of 360 tons of waste daily. A
third furnace is available for standby
operation. A fourth furnace can be
added. The waste storage room has a
capacity of 5,400 cu m. An extra flame
chamber for burning waste oil will be
installed. In the connected boilers
steam of 84 atm. at 450 C will be
produced. They are designed for 27 to
34 tons per hr. The steam goes to a
remote heating station 300 m away. Apart
from the incinerator plant a new autoclave
method for processing sewage sludge is
being developed. The activated
sludge — about 2,000 cu m per week—is
heated up to about 165 C by the hot
sludge coning from the autoclaves.
By adding steam the temperature of the
activated sludge is further raised to
200 F. In the heat exchanger it cools
down again to 65 C. Through this heating-up
process the sludge is sterilized and the
colloid binding of the water is broken. In
a filter press the water contents can then
be reduced to 40 percent. By subsequent
air drying the water contents decreases to
15 to 20 percent. The sludge is ground
and will be utilized for agricultural
purposes. (Text-German)
65-0389
Measures taken in waste incineration plants
to prevent air pollution. Public
Cleansing, 55(9):532, Sept. 1965.
An abstract of a paper by Dr. Karl
Schwartz, presented at the International
Research Croup on Refuse Disposal, held
in 1965 at Trento, Italy is described.
Smoke pollutants, size of incinerator,
meteorological considerations, volatile
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0387-0394
dust and other factors are investigated
with particular reference to German
programs.
65-0390
Midland miscellany. Public Cleansing,
55(2):79-80, Feb. 1965.
Derby, England, has decided on incineration
to solve its landfill area shortage
problems. Because of industrial wastes,
including much ash from local power
stations, disposal sites are at a
premium. A 210 ton per day total-
incineration unit, fully automated with
mechanical grates is projected. In Long
Eaton, England, an increase in salvage
demand was felt to be based on a
temporary 15 percent import tariff and
didn't justify increased salvage drives.
The collection of refuse after public
holidays in Sedgley, England, was
expedited by distribution of paper bags
to handle the additional refuse.
65-0391
New incinerators for greater London.
Public Cleansing, 55(12):663-664,
Dec. 1965.
The significance of the Greater London
Council's decision to build two 1,000
ton per day power-generating incineration
plants with total incineration cost
including loan charges to be met
substantially by power sales is explained.
The proposed capital expenditure is $31
million dollars for the two plants.
pushbutton ignition, and timer control
can be furnished. The one-eighth-inch
MS plate casing is lined with 3-in.
pre-cast refractory slabs. All furnace
castings are made with heat-resistant cast
iron. The 3,000 Ib incinerator is
delivered to the site already assembled,
although it can be supplied in sections
where access is difficult.
65-0393
Perreten, R, T. R. Jeheber, and E. Guex.
Loading wharf and treatment plant for
urban wastes, Geneva. Bulletin Technique
de la Suisse Romande, 91(15) :229-242 ,
Julv 1965.
Details are given for the design and
construction of solid waste loading and
unloading wharfs and the associated
incinerator. The incineration plant,
which began operation January, 1966, is
located downstream from the loading
wharf and provides an inlet canal leading
to elevators for the barges. The elevated
barges are unloaded by a series of grapples
on a moving track which then dump the
solid wastes into storage silos or into
a feed hopper. This plant also receives
solid waste directly from trucks. Sludge is
discharged into basins. The loading wharf,
situated upstream on the junction of the
Rhone and Arve Rivers, provides for the
dumping of solid wastes from trucks directly
into barges in a canal below. Five trucks
can be dumped simultaneously. The theory of
construction and the construction materials
for both wharfs and their adjacent working
areas are discussed. (Text-French)
65-0392
New refuse burner. Waste Trade World,
106(8):27, Feb. 20, 1965.
A new burner for general refuse with a
charge capacity of 6 cu ft and a rating
of 80 Ib of general refuse per hr,
suitable for use in schools, supermarkets,
small hospitals, and otels, has been
announced by A. B. Scorer Ltd. of Manchester.
This latest development called the Scorer
C63, complies with the Clean Air Act through
the provision of a water trough dust
settling chamber and gas-fired afterburner
or ienition burners capable of being fitted
to suit the type of refuse. The fire bars
are designed to give maximum cooling. If
required, flame failure controls, electric
65-0394
Riedlinger, R. A. The waste incinerator
plant in Dusseldorf, West Germany.
Elektrizitaetswirtschaft, 64(24):682-684,
Nov. 1965.
Since 1954 a departure from dumping waste
has been contemplated in Dusseldorf.
Composting of accumulating waste was
discontinued because there is not enough
agricultural area around Dusseldorf to
provide a market for fertilizer. An
experimental incinerator with roller
grates was established to furnish data for
construction of a large four-furnace plant,
which will be completed by early 1966
and will operate continuously to eliminate
the 220,000 to 230,000 tons of waste
accumulating annually. Flue gas heat
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Incineration Europe
will be used to produce steam. The scrap
will be removed from the ash, packaged,
and sold. The ash will be separated
into various grain sizes and sold too.
Only glass-containing ash will be dumped.
The plant is composed of storage building,
incinerator building, ash-processing and
scrap-packaging building, building for
the personnel and offices, and an entrance
building. There is room for 12 vehicles to
empty their loads simultaneously. Each
furnace will burn 10 tons of waste per hr
between 900 and 1000 C and produce up to
16 tons of steam per hr. A layout, cross
section, and illustrations of the plant
are included. (Text-German)
sent a load of insulated cable for test
purposes, at which its officials were
present, which left the metal quite clean.
Another example given is that of Messrs.
Peglars, of Doncaster, Yorks., where the
Sealed Flame Unit is used for recovering
metal from plastic coated castings. A
further advantage, say the manufacturers,
is that customers now have the option to
either buy or rent at a nominal figure,
adding that rental will often be found
cheaper than recurring expensive repairs
to their present inefficient incinerators.
65-0395
Roll waste incinerators for foreign
countries. Schweizerische Bauzeitung,
83(46):856, Nov. 18, 1965.
The city of Nurnberg will receive a waste
incinerator with three furnace-boiler
units handling 300 tons of waste per day
each. Steam for electric power will be
generated. Shortly after Osaka, Japan, made
operational its Von Roll incinerator,
Nihon De Roll Y.K., a subsidary of Von
Roll AG, received an order for an
incinerator for the city of Kyoto. It
will consist of two furnace-boiler units
handling 200 tons per day each. The
steam generated will be used for heating
purposes. Both plants will meet
stringent requirements of the air and
water pollution control regulations.
(Text-German)
65-0396
Smokeless incineration. Waste Trade World,
107(15) :7, Oct. 9, 1965.
Designed mainly for the smokeless disposal
of refuse, the patented Sealed Flame
Disposal Unit, manufactured by Universal
Machinery and Services Ltd. , and now
available on rental terms, is also being
used for clean metal reclamation, says the
firm, particularly in the burning-off of
insulated cable and metal recovery from
plastic-coated castings. The firm
claims that the unit takes everything in its
stride smokelessly, and that every
incinerator carries with it a positive
guarantee to that effect and that the
performance will meet every facet of the
Clean Air Act, even when operated
by unskilled labor. The Home Office recently
65-0397
Smokeless incinerators burn up to 1 ton
per hour. Engineering, 200(5194):59Q,
Nov. 5, 1965.
Recently announced by Riley (1C) Products
Limited, London WC1, is the refuse reducer
shown. It is an addition to the company's
range of Riley-Pillatt incinerators and
Gaserators and is said to be suitable for
burning industrial and household wastes
without smoke at rates of up to 1 ton per
hr. Two basic designs are produced, having
one or two primary combustion chambers. Each
primary chamber is a high tunnel shaped
compartment with a cast iron grate formed
of independent replaceable firebars. The
grate is set low for easy charging and
the fire bar spacing may be varied. The
cast iron charging door is recessed to
take refractory lining and ground on its
sealing face to mate with the cast iron
door frame. It measures 2 ft by 4 ft
and is hinged vertically. It is also
used for ashing out above and below the
grate. A top mounted forced draught fan
provides both primary and secondary
combustion air through external ducting
and nozzles, dampers affording independent
air adjustment. Where two primary
combustion chambers are provided, they are
arranged side by side. The secondary
combustion chamber with a solid hearth
is situated immediately behind. It has
a door similar to that in the primary
chamber so that large objects that could
interfere with combustion in the primary
chamber can be disposed of at a slower
rate. Products of combustion from both
chambers are concentrated in a venturishaped
orifice with refractory lining. A
Riley Mk.1 oil burner plays a brilliant
flame into the orifice to burn any
remaining hydrocarbons. The burner is
controlled by a thermocouple.
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0395-0400
65-0398
Stirrup, F. L. Incineration. In Public
cleansing; refuse disposal. Oxford, The
Institute of Public Cleansing, 1965.
p.87-118.
The advantages of incineration are complete
destruction of combustible and organic
matter, reduction of bulk, ability to
operate under hygienic conditions, freedom
from weather conditions, and use of
residual heat. Disadvantages are need to
dispose of furnace residue and unsuitable
bulk, high costs, and air pollution. The
basic incineration unit consists of cells,
each consisting of a grate beneath a
central feed opening. The receiving
hopper either contains 'a conveyor or is
composed of a simple pit from which refuse
would be lifted by a grab. Dust and
cinder is screened. Electromagnets remove
the metals. The tailing conveyor carries
the remaining to the furnace openings.
Air-borne dust is extracted. The Heenan
and Froude plant gives variable grate
capacity by increasing the number of
cells. Hot gases are drawn away in the
Volund furnace. Stepped grates assist
the early drying, ignition, and final
combustion processes. The L. de Roll
furnace provides for continuous feed via
a drying hearth. The Nichols perfection
grate is an American rocker type, batch
fed, stoker grate built in cells with
individual removable grate teeth
selections. The Nichols Fuller
reciprocating grate, also American,
provides for continuous feed, moisture
evaporation, burning and clinker removal.
The refractory lining of the furnace must
provide a perfect insulation and withstand
heat. Firebrick is the basic liner.
Furnace construction should allow for
expansion and a thorough warming process.
Some steam and burning material are used
for power production, electricity
generation, and waste heat.
65-0399
Tanner, R. The development of Von Roll
incinerators. Schweizerische Bauzeitung,
83(16):251-260, Apr. 22, 1965.
In 1945, the most modern incinerator was
without doubt the rotating furnace by
Volund. Von Roll was licensed to construct
them. But the system had many shortcomings.
Fresh waste was dried by hot gases,
lighted and partly burned. In the
rotating drum the incineration was
completed. The hot gases were returned
to the flame chamber by way of a bypass
duct. This was soon abandoned and the
entire waste gas was used for drying. The
expensive drum was exchanged for a vertical
flame chamber whereby the dimensions of the
incinerator were reduced. The grates
were made of highly heat-resistant
material. Powerful gas-tight hydraulic
mechanics were developed for driving
the grate. Water-cooled slag generators
were installed and the slag removal was
mechanized. Another improvement of this
system consisted in arranging the drying
grate and the main grate behind each
other rather than one above the other.
Further developments made it possible to
adjust the incineration process to the
composition of the waste and permitted the
regulation of the temperature in the
flame chamber. By mixing several kinds
of waste a. better heating value could be
achieved. The boiler size was matched
with the capacity of the grate. Next,
the boiler was placed above the flame
chamber. Blades were attached to the
grate, which hit the slag in an adjustable
rhythm to free it from the surrounding
ashes so that it can burn down completely,
which is essential for a later sanitary
dumping. A number of Von Roll incinerators
are described and illustrated schematically.
Some statistics about the composition of
waste and data on the operation of
incinerators are presented in diagrams.
(Text-German)
65-0400
Tip 'top city' gets new refuse disposal
plant. Public Cleansing, 55(3) : 151-154,
Mar. 1965.
Bradford, England, which has used
sanitary landfills for crude refuse
for about 50 years, has installed a new
separation-incineration plant to conserve
landfill sites. The new plant and its
facilities and method of operation are
described. Refuse, dumped in an
enclosed area into a 100 cu yd hopper,
is first screened for dust and cinder,
the cinders being used for heating the
plant. The manual and magnetic
separation take place followed by
incineration in one of 5 cell-type
incinerators with hydraulically-operated
grates. Clinker is collected in a
travelling ship, then conveyed to a
'buffer storage point for truck collection.
Cost of the unit was $1,200,000.
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Incineration—Europe
65-0401
Tope, 0. Requirements for small domestic
incinerators. Staedtehygiene, 16(6) :141,
June 1965.
To prevent further pollution of the air,
domestic incinerators should only be
installed when urgently needed, such as in
hospitals and in department stores rfhere an
enormous amount of packing material is to
be burned. Ac the installation of such
a plant attention must be paid that each
furnace receives its own chimney which
must be built with especially resistant
material when flue gas temperatures
of more than 400 C are to be expected.
The waste run-down from the various floors
must be shielded off against penetration
of flames and smoke. The incinerator
must burn the waste entirely. An
adjustable gas burner can be installed
to achieve this goal. Additional
equipment is necessary to prevent unburned
material from escaping. Essentially the
VDI (Association of German Engineers)
recommendation 2301 and DIN 18160 must
be observed. (Text-German)
65-0402
Waste incineration and sintering plant
for Berlin Ruhleban. Staedtehygiene,
16(1) :16-17, Jan. 1965.
Berlin is converting from waste disposal
by dumping to incineration and subsequent
sintering of the remaining slag mainly
because it has; no more deposition sites.
Composting cannot be taken into
consideration because the city has no
market for it. Construction work for
the incinerator plant began in October
1964 and will be completed by 1968. The
plant will be able to burn about 2,000
tons of waste within 24 hr and to produce
1 ,000 tons of sintered material which
the construction industry badly needs.
(Text-German)
compiled in a table with all the necessary
data. Basically, six different types
of grate and furnace systems are in use,
such as the travelling grate, roller
grate, Lurgi furnace, etc. Annually,
1.8 million tons of waste can be burned
which corresponds to an amount of waste
of approximately 7.2 x 10 to the sixth
power inhabitants. The plants still under
construction will be completed by 1970,
so that about 3 million tons per year will
be incinerated, equal to the wastes of about
20 percent of the present population of
Germany. Large plants will also
incinerate industrial wastes. The plant
in Essen-Karnap is experimenting with
industrial wastes at the present time.
(Text-German)
65-0404
The waste incinerator in Munich.
Elektrizitaetswirtschaft. 64(7):184,
Mar. 1965.
The waste incinerator in Munich between
July 1964 and January 1965 burned
200,000 cu m of domestic waste--35
percent of the waste accumulated in this
period. After complftion of the second
construction stage, expected in June 1966,
all waste in Munich will be burned in
this incinerator plant. (Text-German)
65-0405
The waste incinerator plant of the city of
Den Haag. Schweizerische Bauzeitung,
83(12):203, Mar. 25, 1965.
The waste incinerator plant in Den Haag
is to be built by Von Roll AG, Zurich.
Three furnaces will burn more than 1,000
tons of waste daily. The steam will be
used for producing electricity and the
generators will yield 25,000 kilowatts of
electric power. (Text-German)
65-0403
Waste incineration in Germany.
Brennstoff-Waerme-Kraft, 17(12):594-595,
Dec. 1965.
In the course of a meeting arranged by
the Institute for Water Supply and Water
Quality in Stuttgart, Germany, a survey
was given on the waste incinerator plants
presently in operation or under
construction in Germany. They are
65-0406
Wolf, M., and J. W. Jacobi. Waste
incineration. Brennstoff-Waerme-Kraft,
17(4) = 186-187, Apr. 1965.
Literature published in 1964 in the area
of waste incineration is listed and briefly
characterized. The journals scanned
are: VDI-Nachrichten, 01- und Gasfeuerung,
Handelsblatt, Mitteilungen Verein,
Grosskesselberitzer, Staedtetag, 2'tg
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0401-0409
kommun, Wirtschaft, Staedtehygiene,
Kommunalwirtschaft, Brennstoff-Waerme-Kraft,
and VDI-Zeitschrift. The list of
references contains 39 titles. (Text-German)
65-0407
Wotschke, J. The development of the
flame chamber melting method.
Brennstoff-Waerme-Kraft, 17(8):379-382,
Aug. 1965.
Several experiments were made with an
incinerator operating according to the
flame chamber melting method. The
incinerator was filled with wetted ash
to test its functioning with this almost
noncombustible material; 1,380 C was
necessary to melt the material in the
flame chamber. The temperature
characteristic during the heating up period
is illustrated in a diagram. In a
second experiment the incinerator was
filled with very heterogeneous industrial
wastes with a high amount of plastic
material; 15 minutes after ignition the
material began to melt; 1 hr afterwards
all auxiliary burners were turned off.
After the second hour all ventilators
and auxiliary mechanism failed. Four hours
later the disabled parts were repaired. The
incineration process could be continued
just by blowing air onto the still glowing
waste; no auxiliary burners were required.
The temperature characteristic during this
process is illustrated in a diagram.
Afterburner temperatures of 1,550 C to
1,600 C were measured. Incinerator
capacity is 2 to 20 Gcal per hr.
Continuous operation was impossible
because of high thermal stress in the flame
chamber and clogging of the loading duct.
Construction changes to improve
performance are being worked out. A
schematic and description of the incinerator
is given. (Text-German)
650408
Wuthrich, F., and R. Ropp. Electromechanical
equipment for an incineration plant for
household wastes in the City of Geneva.
Bulletin Technique de la Suisse Romande,
91(15):243-250, July 1965.
The citie-r of Villette, Richeliun, and
Geneva did a study of solid waste disposal,
with the resulting order of an incineration
plant made by Von Roll. Situated next to
a hydroelectric plant, it is designed to
receive solid waste from barges or from
trucks. Truck wastes, which may contain
bulky trash such as mattresses and wac,Mr-f,
machines, are passed through a
pulverising chopper before being cycled
with the wastes delivered by barge. All
wastes are then lifted by clamshell buckets
and dumped onto a vibrating feed hopper.
The plant is equipped with two furnaces,
each capablt of incinerating 200 ton
of wastes each day. The wastes are fed
into the furnaces by the vibrating feed
hopper, which is automatically controlled
by an apparatus with radioactive rays,
situated in the cooling shafts. The wastes
catch fire at the end of the feed grill
and fall onto the principal grill which,
through a system of flipping bars,
regulates the incineration and drops the
cinders down into a canal filled with
water. This residue is then transported
to a storage silo for later removal. The
hot fumes generated are passed through a
heater to reduce corrosion, a heat
exchanger, and dust filters to remove flying
cinders. Special problems discussed in
detail are, chimney height and fume
abatement, burning of used oils, clamshell
buckets, pulverising chopper, and
incineration of household wastes with
dried sludge. Combustion parameters of
the furnaces are also discussed.
(Text-French)
INDUSTRIAL WASTES
65 0409
Amberg, H. R. Aerated stabilization of
board mill white water. In Proceedings;
20th Industrial Waste Conference, Lafayette,
Ind., May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.525-537.
Waste treatment measures have been put
into effect at the plant in Baltimore,
Ohio, to improve water quality in the
receiving stream, Little Walnut Creek. The
mill there produces 150 to 200 tons of
board and corrugating medium per day. The
major source of BOD containing waste is
the white water from the two paper machines.
Marx Saveall and primary sedimentation
lagoons remove an average of 5,811 Ib of
suspended solids per day or 88.9 percent
of the suspended solids total. The average
BOD reduction by primary treatment was
1,850 Ib per dav or 21 percent of the total
load. The aeration lagoon removed about
5,000 Ib per BOD per day. This was an
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Industrial Wastes
average of 81 percent of the load applied
to the unit. The effluent had a suspended
solids content of 265 ppro and an average
BOD of 97 ppm. Removal of the suspended
solids by sedimentation resulted in an
additional BOD reduction of about 48
ppm, making a total reduction of about
91 percent. The four surface aerators added
about 5,000 Ib of DO per day. The average
aeration efficiency was 1.74 Ib of
oxygen per hp-hr. The aeration basin,
operated as a completely mixed system,
was very effective in handling wide
fluctuations in daily BOD load. Although
there was a 2.4-fold increase in BOD load
the aeration basin during the 4-day survey
period, the quality of the effluent was
not significantly changed. Operating
costs are $0.72 per ton of production or
$0.0162 per Ib of BOD removed.
65-0410
Andelman, J. B., M. A. Shapiro, and T.
C. Ruppel. Determination of organics in
water. In Proceedings; 20th Industrial
Waste Conference, Lafayette, Ind., May
4-6, 1965. Purdue University Engineering
Extension Series No. 118. p.220-234.
The organic constituents of water supplies
were concentrated by passing the water
through an activated carbon column on
which the organic constituents are adsorbed.
Organic water content has then been related
to taste and odor. The degree of
pollution of rivers has thus been compared.
The extent of recoverability of organics as
affected by the air-drying process was
also assessed. Tap water from one of
the three municipal water supplies was
passed through an activated carbon filter
at the rate of 0.25 to 0.5 gpm. A
principal aim was the development of
techniques for identification of specific
organic chemicals, rather than the
measurement of a total weight of recoverable
material. Extracting solvents which
could be removed from the extracted
organics by vacuum distillation at room
temperature or below were used. To
determine the effect of air-drying the
water-wet activated carbon on the recovery
of organics, aqueous solutions of
acetophenone (B.P. 202 C), one of the
contaminants found in river water, were
equilibrated with activated carbon. Wet and
dry extractions of carbon with pyridine
were carried out. Any volatile organics
that might be removed with water-wet
activated carbon as they evaporate during
the drying process were measured. Gas
chromatography was chosen as the analytical
technique. A summary of acetophenone
extractions from wet and air-dried
carbon indicates that, within experimental
error, there is no essential difference
between the two techniques, either by
using a single (62 to 65% recovery) or
two successive (81 to 85% recovery)
extractions of different aliquots of
carbon with the same portion of solvent.
An unexpected result was that the average
of the two successive extractions implies
that the second had extracted essentially
all of the acetophenone from its aliquot
of carbon.
65-0411
Application of digested sludge to land.
Water and Waste Treatment, 10(10).:519,
Nov.-Dec. 1965.
There is some question as to the value
of sludge manure as a fertilizer. A
paper presented by E. G. Coker at a
recent meeting of the Institute of Sewage
Purification in Bournemouth gave
authoritative backing to the claims that
sewage sludge has value as a manure. This
work was based on a full-scale investigation
in which the liquid digested sludge was
applied at rates that provide nutrients
in the same amounts as artificial
fertilizer. The sludge was high in
nitrogen and low in potash and was used
in two trials with grass and one with
barley. In all the trials, the dry weight
increase of grass straw and grain was the
same with the sludge and with artificial
fertilizer. On pure ryegrass sward the
upper limit of useful nitrogen was an
application of 300 Ib per acre per year.
Sludge produced 86 percent of the protein
produced by artificial fertilizer nitrogen.
Toxic effects from zinc and chromium in
sludge have damaged crops which have had
repeated heavy applications of dried sludge
and sludge cake on acid soil. If the
liquid sludge is applied at rates giving
normal agricultural quantities of
nitrogen (5,000 to 7,000 gal per acre),
and not too frequently, there should be
little hazard from the toxic metals.
65-0412
Armour, J. Municipal engineering in the
United Kingdom. In American Public Works
Association Yearbook, 1965. Chicago,
American Public Works Association.
p.212-224.
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0410-0414
The history of municipal engineering in
the United Kingdom is traced, noting the
ori°in of the functions of the municipal
engineer and the authority he serves. The
municipal engineer serves a wide variety
of different authorities: England, Wales,
and Scotland have over 1,700 local
authorities. Sludge continues to be a
problem and heated sludge digestion is
extensively employed and the sludge gas
produced is used for heating and power
production. Although most of the digested
sludge is dried, there is very little demand
for it. Plants have been built to convert
sewage sludge mixed with municipal refuse
into compost. Many British cities near the
coast or vanigable rivers have special
ships to dump sludge in deep water offshore,
providing an economical solution to the
problem. A pilot plant is being carried out
at Portsmouth to give electrolytic
treatment up to 300,000 gal of sewage per day.
The new sewage works at Glasgow employs
the activated sludge process, surface
aeration type.
65-0413
Ayers, K. C., K. S. Shumate, and G. P.
Hanna. Toxicity of copper to activated
sludge. In Proceedings; 20th Industrial
Waste Conference, Lafayette, Ind., May
4-6, 1965. Purdue University Engineering
Extension Series No. 118. p.516-524.
Experiments were carried out to test
various hypotheses as to the mechanisms of
copper toxicity and to provide the basis
for more significant interpretations of
the observed effects of toxicity than have
been possible. When copper-bearing
sewage enters the aeration tank in the
activated sewage process, there is a rapid
redistribution of copper between the
various available ligends (components
capable of forming complexes with metal
ions). Because of the insolubility of
copper hydroxide at the pH values present,
over 7.0, most of the copper will be
in the form of the hydroxide or as a
stable copper-ligend complex. A relatively
constant proportion of the copper forms
stable inactive complexes with sensitive
cell components, e.g. respiratory enzymes.
Any direct effects from the formation
of metabolically inactive complexes would
be observed immediately. The observed linear
decrease in respiratory activity would be
expected. The overall copper equilibrium
in the aeration tank, and therefore, the
degree of toxic effect will depend on
three independent variables reflecting
either copper or ligend concentrations:
copper dosage, mixed liquor suspended
solids, and influent sewage strength. It
was therefore reasonable to find a
relationship between each of these three
variables and the three toxic effects as
was reflected in the regression
equations developed from the data. It is
hypothesized that the metabolically inactive
copper complexes may be reversed by dilution
or by the addition of uncomplexed ligends.
On being set free from the complex, the
ligend (e.g. a respiratory enzyme) may
revert to a metabolically active
state. So the drop in respiratory rate
due to copper dosage should stop soon after
the dosage is stopped. This has been
observed to be true.
65-0414
Azad, H. S., and D. L. King. Evaluating
the effect of industrial wastes on lagoon
biota. In Proceedings; 20th Industrial
Waste Conference, Lafayette, Ind., May
4-6, 1965. Engineering Extension Series
No. 118. p.410-422.
The toxic substances considered were
copper, added as copper sulfate, and
chromium, added as potassium dichromate.
Copper is a common component of
electroplating wastes and is widely used
as copper sulfate to control the growth of
unwanted aquatic plants. Chromium gets
into treatment plants from many sources
ranging from plating wastes to treatment
for corrosion inhibition. The samples
used were taken from the effluent of a
bench-scale lagoon which is a 1-ft-sq
plexiglass tank. The total volume of the
lagoon was maintained at 20 liters and
it was operated on a fill-and-draw
basis for a detention time of 20 times
with a loading of about 20 Ib of B.O.D.
per acre per day. The material fed was a
synthetic sewage which has been used to
maintain balanced biotic populations in
a variety of laboratory treatment facilities.
Copper sulfate in concentrations greater
than 0.20 mg per liter seriously affect the
performance of a waste-stabilization
lagoon. Shock loads of hexavalent
chromium at concentrations of up to 40
mg per liter were shown not to have an
appreciable effect on lagoon performance.
Slug doses of copper greater than 2.0
mg per and of chromium greater than 50
mg per liter reacted with the natural
buffer system of the lagoon causing a
significant depression of pH. This was
accompanied by a gas which appeared to be
carbon dioxide.
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65-0415
Backmeyer, D. P. Liquid sludge disposal
at Miami, Florida. Compost Science,
6(2):10-11 , Summer 1965.
The city of Miami treatment plant was
placed in operation in Oct. 1956. It
operates with four sludge digesters which
convert about 40 percent of the original
solids removed into gas. This gas is
used as fuel for the compressors. After
digestion, disposal is achieved by vacuum
filtration and incineration. The
incinerators were not operated during the
first 3 years of operation because of
excessive costs; the cake was allowed to
air dry. It was shown in 1959 that the
sludge could be applied to the plant yard
and non-tidal lagoons in liquid form and
in April 1961, the dewaterinp, operation
was discontinued. This simple and inexpensive
method was applied with very good results.
Additional land has been made available
for drying and storing the sludge. The
dried-sludge is removed by bulldozer and
placed in stock piles, available for use as
a soil builder when the land is developed
at a future dste.
65-0416
Barbaro, R. D., and J. V. Hunter. The
effect of clay minerals on surfactant
biodegradability. In Proceedings; 20th
Industrial Waste Conference, Lafayette,
Ind. , May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.189-196.
The removal of surface active agents from
water supplies may be achieved by the
adsorption of surfactants onto particulate
matter, under natural or artificial
conditions. Commonly found clay minerals
such as kaolinite and bentonite are being
evaluated by the Public Health Service as
adsorbents. The test materials included
a relatively degradable species (anionic
Igopon T-77, the non-ionic Lauryl alcohol
adduct and cationic cetylpyridinium bromide)
and a relatively nondegradable anionic
species (Ultra^et K) . Twenty pp*n solutions
of the test surfactant and distilled
water blanks were shaken with zero, 100,
and 10,000 ppm of the homoionic hydrogen
forms of both kaolinite and bentonite.
After shaking for 2 weeks, 50 ml aliquots
of the solutions were added to nutrients
and buffer solution at pH 7.2. Enough
activated sludge seed was added to bring
the concentration to 100 ppm on a
suspended solids basis. The characteristics
of the homoionic hydrogen forms of both
kaolinite and bentonite are shown in a
table. Particle size distribution is
described. Graphs show: oxygen
utilization for 20 ppm anionic surfactant,
20 ppm non-ionic surfactant, and 20 ppm
cationic surfactant solutions in the
presence of varying amounts of clay
minerals. All relatively degradable systems
except the Igepon T-77-kaolinite showed
a marked decrease in oxygen utilization
with increase in concentration of both
kaolininte and bentonite. The biological
utilization of relatively degradable species
of the three types of surfactants may be
inhibited by small quantities of kaolinite
or bentonite. This inhibition of
substrate utilization is greatest in the
bentonite systems. No significant effect
of clay particles upon the utilization of
the relatively nondegradable species of the
three types of surfactants could be shown by
this technique.
65-0417
Bennett, G. F., and L. L. Kempe, Oxygen
transfer in biological systems. In
Proceedings; 20th Industrial Waste
Conference, Lafayette, Ind., May 4-6, 1965.
Purdue University Engineering Extension
Series No. 118. p.435-449.
Pseudomonas ovalis NRRL B-8 elaborates
gluconic acid when suspended in a glucose
medium that is aerated. This reaction
is glucose + oxygen yields gluconic acid.
The present study confirmed that in a
resting cell suspension (no nitrogen)
99 percent of the glucose fermented is
converted into gluconic acid by this
organism. The experimental conditions
are given in detail. The oxygen transfer
rate in an unsparged, but agitated
system was found to be less than the
oxygen transfer rate in a system that is
both sparged and agitated at the same time.
The differences between these two
measurements increase as the gas-liquid
interface of the partial pressure of
oxygen in the gas is increased. The
data suggest that there are two parallel
paths for the transfer of oxygen from air
to the cell. In the unsparged liquid, the
microorganism has only the oxygen dissolved
in the liquid and only one path is operative.
In a sparged system, another path becomes
important. Some of the cells adsorb on
air bubbles, or air bubbles adsorb on cells,
with a consequent merging of the liquid
films. This intimate contact provides a
path for direct transfer of oxygen,
96
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0415-0420
thereby circumventing diffusional resistance
of the bulk of the liquid and of one of
the liquid films. Some of the resistance
to oxygen transfer is reduced for some
of the cells by this process and increased
oxygen transfer is promoted even when the
dissolved oxygen concentration is well
above the critical value. The value of
gas-cell contact is thus evident.
65-0418
Bloodgood, D. E. Twenty years of industrial
waste treatment. In Proceedings; 20th
Industrial Waste Conference, Lafayette,
Inr)., May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.182-188.
Trends in the disposal of wastes of the
milk, packinghouse, metal plating, brewing,
canning, petroleum, paper and pulp, oil,
coal, and steel pickling industries are
traced for the last 20 years. The number
of articles dealing with specific industrial
wastes has decreased. Twenty years ago
a milk loss of 2 percent was common; today
a milk plant cannot operate economically
with a loss more than -, of 1 percent. Whey,
which was formerly a waste product in cheese
plants is now made into usable food
products. Spraying industrial wastes on
land is now a successful method of
disposal. Two decades ago, most
packing-plant wastes were handled
satisfactorily in municipal sewer systems,
but now the adaptation of the anaerobic
decomposition process is necessary to
alleviate this problem. Through education
the metal-plating industry has becon>
aware of the economic loss of plating
solutions. The brewing industry, like
the distilling industry, has employed
waste-saving devices. Sodium nitrate has
been used to control odorous lagoons in
the canning industry, and spray irrigation
has also been utilized. In the petroleum
industry, an oil separator of high
efficiency has been developed. The
stabilization pond has been used for the
wastes of antibiotics. Paper and pulp
mills, confronted with large quantities
of wood sugars and color matter, have
developed a process for the production
of yeast from the sugar. The use of brine
injection has increased oil production.
Progress is being made in coal mine
drainage. Several processes have been
developed for the neutralization and the
disposal of pickling liquors in the
pickling of steel. Other wastes discussed
are: pesticides, commercial detergents,
and poultry.
65-0419
Blosser, R. 0., and A. L. Caron.
Centrifugal dewatering of primary paper
industry sludge. In Proceedings; 20th
Industrial Waste Conference, Lafayette,
Ind., May 4-6, 1965. Engineering Extension
Series No. 118. p.450-456.
A diagramatic representation of a
horizontal conveyor-type centrifuge is
given. Slurry to be dewatered enters
through the center of a revolving bowl.
The magnified gravitational force created
by rotation induces suspended solids to
accumulate on the bowl wall. A helical
rotating in the same direction but at a
slightly different speed than the bowl
conveys solids along the bowl and up an
inclined breach through suitably located
ports. Clarified liquid is discharged
through adjustable weirs located at the
opposite end of the device. The increase
in centrifugal force obtained by increasing
bowl speed results in better solids
recovery efficiency. The higher bowl
speed resulted in an increased solids
recovery of 4.4 percent at 1,400 gph and
5.3 percent at 4,500 gph. In every case
the higher speed produced the better
solids recovery. An increase of from
1.1 percent to 3.3 percent in solids
recovery efficiency was found when bowl
water depth was increased from Qi to
maximum depth level. There was some
sacrifice in cake dryness resulting in a
drop of from 1 to 4 percent in cake
solids content. It is important to
concentrate the sludge to the highest
practical consistency before centrifuging. A
drop in fed slurry dry solids from 2.18 to
1.12 percent resulted ir a solids recovery
efficiency drop of from 92 to 89.3 percent.
The factors that must be maintained at a
maximum for optimum results are therefore,
bowl speed, detention time, and fed sludge
consistency. The equipment has
limitations: trash in the form of large
chips and sticks cannot be handled
(screens can eliminate this) ; flow rates
must be held at a low level on a gpm to
horsepower ratio to obtain good solids
recovery. Advantages are: little
supervision required; ability to handle
a wide variation in fed sludge consistency;
lox^ space requirement; no need for chemical
conditioning. Costs are competitive with
vacuum filtration.
65-0420
Boegly, W. J., R. L. Bradshaw, F. M.
Empsom, et al. Project salt vault:
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Industrial Wastes
radioactive waste disposal in a salt
mine. In Proceedings; 20th Industrial
Waste Conference, Lafayette, Ind., May
4-6, 1965. Purdue University Engineering
Extension Series No. 118. p.398-409.
The fuel assemblies, after canning in
Idaho, will be shipped on a
specially-designed truck-trailer
(illustrated) to Lyons, Kansas. There
the carrier will be removed and placed
vertically over a steel-cased charging
shaft which extends to the mine working
area about 1 ,000 ft below. The fuel
cannisters will be lowered one at a time
down the 19.1 in. waste charging shaft
into a shielded cask, mounted on an
underground fuel assembly transporter. The
transporter will then move to the
experimental area and the fuel canister
will be lowered into a suitably lined and
shielded 12-in. diameter, 13 ft-deep hold.
The in situ heat-transfer properties of
rock salt seem to be close enough to the
laboratory values that confidence can be
placed in theoretical heat-transfer
calculations. Most bedded-salt deposits
contain trapped moisture which is released
by a shattering of the salt at temperatures
above 250 C. This possibility can
be avoided by Limiting the maximum
temperature of the disposal operation
to 200 C. Rock salt is about equal to
concrete for gamma-radiation shielding. A
radiation exposure dose of 5 x 10 to the
eighth power R produces some changes in
the structural properties of rock salt,
one of which is an almost 10 percent
reduction in compressive strength. Because
of the shielding characteristics of
salt, this effect will be limited to the
salt near the radiation source. The
costs of using a salt mine facility for
disposal will be on the order of 0.01
or 0.02 mills per Kwh of electricity
generated.
65-0421
Boubel, R. W. Wood residue incineration
in teepee burners. Circular No. 34.
Corvallis, Oregon State University, 1965.
30 p.
Residue from the lumber and plywood
manufacturing process is usually
incinerated at the mill site in a
tepee-shaped, single-walled, steel waste
burner. Some practical information
concerning combustion in tepee waste
burners is given. This burner is not a
desirable incinerator from an air pollution
standpoint, but by optimizing the combustion
conditions for each individual burner the
pollutants can be minimized. Waste burner
construction maintenance, and cost are
covered. The correct firing of the burner
is delineated. Appendices include1 a Burner
Data Sheet, State of Oregon Regulations,
and analysis of wood fuels.
65-0422
Bramer, H. C., and R. D. Hoak. Some
observations in liquid-solids separations
with particle growth. In Proceedings; 20th
Industrial Waste Conference, Lafayette,
Ind., May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.423-434.
The mechanism of sedimentation with
suspensions of a self-coagulating clay
(kaolin) was investigated using one-liter
Griffin beakers on a Phipps and Bird
multiple stirrer. Each beaker had a
tube at the mid-point of the side wall
for withdrawing samples. Suspensions of
kaolin in distilled water were made by
adding weighed portions to a liter of
water and stirring at 100 rpm for 5
minutes, The solids remaining in
suspension in 250-ml portions were
measured gravimetrically. Portions were
withdrawn after settling times of 1,
5, and 10 minutes from replicate initial
suspensions of 100, 500, and 1,000 ppm.
Settling rates were determined: (1)
during quiescent settling after initial
mixing; (2) during quiescent settling,
following 10 minute of flocculatiori
mixing (20 rpm) after initial mixing; (3)
during mixing at 35 rpm after initial
mixing; and (4) during mixing at 15 rpm
after initial mixing. The data were
analyzed by multiple correlation techniques
o estimate the relative contribution
of each of the independent variables
to the observed sedimentation efficiency.
The multiple regression equation is given.
The coefficient of correlation
of the regression equation was 0.866. The
over-all coefficient of determination was
0.749 and the standard error of estimate
was 12.5. The 75 percent explained
variation was attributed to the independent
variables as follows: initial concentration,
ppm = 18.7 percent; settling time, minute
= 20.9 percent; electrophoretic ability,
micron per second per v per cm = 3.11
percent; electrokinetic current, micron
amps = 15.A percent stirrer speed during
settling, rpm = 20.9 percent, and
flocculation time, minute at 20 rpm = 21.1
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0421-0425
percent. The results are given in three
tables and nine figures and are discussed.
65-0423
Breidenbach, A. W. Surveillance for
chlorinated hydrocarbon pesticides in
surface waters. In Proceedings; 20th
Industrial Waste Conference, Lafayette,
Ind., May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.248-253.
The Public Health Service Water Pollution
Control Surveillance System has 131
surface-water sampling stations on major
waterways and the Great Lakes. Samples are
taken as frequently as several per hr with
some automated water quality equipment
where pollution is a problem to as few
as once or twice a year. Many different
analyses are made. During the period
May through December 1962 either DDT or
dieldrin was identified in 38 samples from
10 rivers. These pesticides were not
identified in the drainage from many
agricultural areas including the Mississippi
and Missouri rivers, but it is possible
that they were present at levels below the
sensitivity of the method used or that
they were adsorbed on the suspended solids.
These suspended solids were at least
partially removed in the carbon adsorption
sampling system then in use. Gas
chromatography (more particularly
microcolometric titration and electron
capture detectors) made it possible
to identify smaller quantities and to
provide additional data to support their
identification. It is now possible to
measure nanogram quantities in a liter
of water. The frequency of occurrence
of six chlorinated hydrocarbon pesticides
in several river basin areas is shown in
a figure. Dieldrin was widespread.
Endrin was relatively prominent in the
southwest lower Mississippi, upper
Mississippi, and Missouri River basins.
DDT and DDE were also relatively
widespread. Heptachlor and aldrin were
noted less frequently. Concentrations
were all in the part-per-trillion range.
These presticides can become adsorbed on
solids and may be expected to be associated
with the suspended solids in water. The
relationship of numerous plankton species
to these pesticides is not understood.
65-0424
Bunch, E. L., and M. B. Ettinger. A
field countercurrent extractor for water
pollutants. In Proceedings; 20th Industrial
Waste Conference, Lafayette, Ind., May
4-6, 1965. Engineering Extension Series
No. 118. p.93-97.
A complete portable liquid extractor has
been fabricated to recover organic
pollutants from surface waters. In
countercurrent extraction, improved
efficiency is obtained by extracting
the weakest sample with pure solvent
and using this solvent to extract
progressively stronger batches of sample.
The countercurrent extractor consists of a
Podbielniak model 600 SP centrifugal
contactor with the necessary pumps and
accessory equipment which extracts water
containing finely divided silt at a combined
flow of 5 gpm. The contactor is a
pressure-tight cylindrical vessel
with 21 perforated hands or 'elements'
inside the rotor which clarify or mix
the light and heavy liquid phases. The
flow of the liquids through the
contactor is described. Water from the
river test location is pumped to a
55-gal drum that serves as a feed tank
and as a clarifier for removing grit.
The turbine pump on the extraction rig
forces the water from the feed tank through
a rotameter, through a flow control
valve, and into the contactor. The flow
of the solvent is described. This unit
should find use in extracting carcinogenic
polynuclear hydrocarbons and pesticides, and
in capturing 'slug' doses of organic
pollutants in river water.
65-0425
Burbank, N. C., and J. S. Kumagai. A
study of pineapple cannery waste. In
Proceedings; 20th Industrial Waste
Conference, Lafayette, Ind., May 4-6,
1965. Purdue University Engineering
Extension Series No. 118. p.365-397.
Two problems were studied: the
variation in waste flows and waste
characteristics for a particv.lpr pineapple
cannery; and the feasibility of treatment
of this waste by laboratory-scale
activated sludge units. The waste-water
conveyance system of a major cannery in
Honolulu consists of a network of ditches
located throughout the process section of
the 56-acre plant. Industrial cooling
waters and low BOD wastes are discharged
into a stream. The remainder of the waste
water, about 20 percent of which bears a
high BOD converges in a single ditch
and discharges into the municipal sewer
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Industrial Wastes
for disposal by ocean outfall. The average
volume of waste discharged ranged from
458 gal to 625 gal per ton of pineapples
processed with a weighed average of 527
gal per ton. The average daily soluble
BOD. discharged ranged from 24.1 to 32.8
Ib per ton with a weighed average of
26.2 Ib per ton. Washwater flows were
generally of 2-hour duration with a
range of 3.7 to 4.2 mgd. The waste
contains high soluble carbohydrates
measurable as sugar by the colorimetric
method. The sugar measured for the
composited samples ranged from 80 percent
to 90 percent of the soluble COD. Sufficient
nitrogen was presented for biological
treatmen: The longterm BOD determination
showed the waste was non-toxic and readily
degradable. For the completely mixed
system, the maximum loading rates of 17.5
sugar per Ib MLSS per day gave 98 percent
sugar removal. The batch-fed fill and
draw units gave high sludge yields in a
range of 65 to 85 percent of the theoretical
oxygen demand for carbohydrates. This
indicated that the batch was being.
actively metabolized. The effluent
from the continuous flow unit was turbid
and odorous throughout the run. The
sludge in both batch and continuous
systems had poor settling characteristics.
Solid-liquid separation by plain
sedimentation would therefore not be
satisfactory. The activated sludge
system is an efficient method of removing
the high soluble sugars from the waste.
65-0426
Buscavage, J. J. Research and
demonstration projects in the abatement
of acid mine drainage. In Proceedings; 20th
Industrial Waste Conference, Lafayette,
Ind., May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.664-672.
The extensive coal mining in Pennsylvania
for more than 150 years has resultec
in approximately 2,000 miles of streams
impaired by the acid and iron in mine
drainage, which are of little or no
value for industrial or public consumption.
The 'Appalachia Bill' was passed by
the U.S. Congress to aid this economically
depressed and mine drainage control
legislation was passed by the Pennsylvania
state legislature. The projects included:
the study of the effect of coal mine drainage
and other industrial wastes upon the
normal chemical, bacteriological, and
other biological processes by which a
stream may free itself of pollution;
the formation and occurrence of acids
in coal mines and other coal workings
and wastes, the development of procedures
for reducing or preventing acid generation:
and pilot plant treatment of coal mine
drainage to neutralize the acid. The
Monongahela River Mine Drainage Remedial
Project strives to determine the sources
and amounts of pollution from coal mines
in this watershed, the means and cost
estimates for improving its quality.
The El Camion Strip Mine Reclamation
Project provides technical information
concerning practical method of restoring
abandoned areas. The Wetmore Coal Study
tests and evaluates various methods of
protecting valuable resources of forest
land and restoring the surface to
productivity after surface mining.
Retreat mining by the Christopher Coal Co. ,
the Toms Run Project, and the Slipper Rock
Creek Survey are discussed. The Coal
Research Board in the Pennsylvania
Department of Nines and mineral
industries has provided $237,000 in the
form of research and grants involving
mine drainage.
650427
Busch, A. W. Energy, total carbon and
oxygen demand. In Proceedings; 20th
Industrial Waste Conference, Lafayette,
Tnd., May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.457-469.
Two procedures for the measurement of
biodegradable organic content In terms
of oxygen equivalents are described. Two
other ways of measuring pollution are
thermodynamic energy change and total
carbon. The validity of applying
thermcdynamic concepts to biological
systems IK questioned. Total carbon
changes during the process of biological
oxidation using a carbon analyzer are an
interesting measurement. In biological
oxidation only soluble organics are of
basic significance either for treatment
process or pollution measurement. The
ease and rapidity (about 2 hr) of the
mass culture technique in conjunction with
the total carbon analyzer offer an
interesting development for definitive
pollution measurements.
65-0428
Cairns, J. Biological concepts and
industrial waste disposal problems. In
Proceedings; 20th Industrial Waste
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0426-0430
Conference, Lafayette, Ind., May 4-6,
1965. Purdue University Engineering
Extension Series No. 118. p.49-59.
Biological concepts may be used to provide
the three basic needs for any waste
disposal design system: (1) a baseline
reference study showing the existing
pre-operation conditions against which
periodic checks may be made; (2) a
continuous monitoring system to check
short-term effects caused by spills or
changes in operating procedures; and (3) a
predictive system by which the effects of
a waste may be measured before its
introduction into the stream itself. The
pre-operation baseline study is depicted
in a series of bar graphs or histograms.
The average number of species obtained by
unit collecting effort in a series of
undisturbed or natural areas is represented
by a column height of 100 percent and
designated a 'healthy station'. Species
are: Column I: Diatoms, blue-green
algae, and green algae known to be tolerant
of pollution. 4 species =100 percent.
Column II: Oligochaetes, leeches, and
pulmonate snails. 6 species = 100 percent.
Column III: protozoa, 41 species = 100
percent. Column IV: diatoms, red algae,
green algae other than those in Column I.
81 species = 100 percent. Column V:
prosobranch snails, triclad worms, and a
few smaller groups. 11 species = 100
percent. Column VI: crustaceans and
insects. 47 species = 100 percent.
Column VII: fish. 20 species = 100
percent The changes resulting from
degrees of pollution from 'healthy',
'semi-healthy', 'polluted', and 'very
polluted' are illustrated in bar graphs.
The biological monitoring system checks
the entire environment whereas a chemical
system monitors only selected portions. A
biological system integrates all the
environmental variables so one sees
their interaction while the chemical
system records each characteristic
separately. Both systems provide useful
information. Monitoring systems are
described and illustrated. Practical
applications of biological concepts are
listed.
65-0429
Canham, R. A. Solids removal in canning
waste. In Proceedings; Conference on
Waste Disposal for Food Processing Plants,
Easton, Md., Jan. 12, 1965. University
of Maryland and U.S. Department of
Agriculture, Mar. 1965. p. 19-26.
The canning industry is fortunate in
many respects when camparing its problems
with other industries. Most canning
operations are seasonal. This allows a
long period of rest or recovery for whatever
system of waste treatment is practiced.
Many canning operations are nearly rural
or are located in small communities. This
allows the consideration of land treatment
because of location. Wastes produced by
most canning operations are non-toxic to
animals and crops. Canning wastes are
generally not harmful to soil. The
seasonal nature of the industry makes it
unsound to capitalize a waste treatment
facility costing in many instances more
than the processing plant. A brief review
of the predominant methods of treatment
of canning waste reveals that lagoons or
stabilization ponds, and spray irrigation are
tlie two most popular choices. Some waste
products now being utilized as stock
feeds are pea vine ensilage, corn husks, cobs,
and trimmings. The almost universal
practice for dealing with solids first
involves separation by screening. It
may be possible to eliminate or make
modifications of the screening process and
still have a sound waste control program.
The possibility of discharging unscreened
waste directly to a relatively small
lagoon, followed by one or more
stabilization ponds in series, is discussed.
Some work was done with an irrigation system
where the solids were disintegrated in a
comminuter and included in the spray system.
This system can be used quite satisfactorily,
although work needs to be done on
development of the disintegration equipment
to break up solids fine enough to prevent
cloggir •: of the nozzles.
65-0430
Carter, H. R. Better activated sludge - by
the Kessener-brush aeration process. Civil
Engineering, 35(12) :67-69 , Dec. 1965.
The process has the advantages of a
shorter retention time, a shorter power
requirement, and a degree of treatment
which should make it of interest to
engineers everywhere. It is a time-tested
process (perhaps originated around 1914)
and its value has been increased bv recent
improvements. Although more susceptible
to upset from shock overloadings than its
counterpart, the trickling filter, the
activated sludge process has become
increasingly popular during the last fifty
years because of the flexibility of
operation and its small land requirements.
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Its hygienic ad-vantages are odor and fly
reduction. The oxygen supply needed has
been supplied by diffused air or
mechanical aeration devices, and there
have been many variations in the equipment
used in both these broad classifications.
The Kessener brush aerator is a mechanical
surface aerator. The history of the
Kessenger devices is described and schematic
drawings illustrate the flow in different
models. Kessener emphasized not only the
design of the brush rotor but also the
geometric configuration of the tank in
his work. The latest version of the brush
rotor is described and the practical
results at various sites reported.
65-0431
Cooke, W. B. Fungi in sludge digesters.
In Proceedings; 20th Industrial Waste
Conference, Lafayette, Ind., May 4-6,
1965. Purdue University Engineering
Extension Series No. 118. p.6-17.
Two digestors were operated during the
first experiment. A slurry of fish meal-
was mixed with raw sewage, settler! in a
flow-through tank and the resulting primary
settled slurije added daily to one
digestor as daily samples were removed
for determination of quality and activity.
A second portion of the settled mixture
of raw sewage sludge and fish meal
was fed to an activated sludge system from
which excess secondary sludge was
removed, mixed with the previously
described primary sludge and the mixture
fed to a second sludge digestor. Both
digestors were operated as continuous
digestors with a detention time of 16
days. They produced an average of about
700 ml of gas per g of volatile solids fed.
Reduction of volatile solids was satisfactory.
Six isolation methods were used. Thirty-one
sets of samples of primary settled and
digested sludges were processed. Of
the 66 species isolated, 15 were found
fairly constantly throughout the series
and more frequently toward the end.
Thus a population adapted to survival
or growth in the environmental conditions
of the sludge digestor was in the piocess
of being selected. The yeasts and molds
still present after three complete turnovers
indicate that they may be taking part
in the digestion process by obtaining
nutrients for growth rather than merely
being present in the quiescent state.
After the development of a stable
sludge-digestion system, many yeasts
and molds are present. The use of
sterile and non-sterile fish meal as a
substitute for sewage solids furnished
an adequate substrate for growth
of filamentous fungi and for maintenance
of a sludge which was still adequately
digesting after 7 complete turnovers.
Fungi, including yeasts and molds, are
members of a population of miscellaneous
microorganisms in sludge digestors as
has been demonstrated in both pilot
laboratory-scale digestors and in operating
sludge digestors.
65-0432
Cooper, F., E. Hindin, and G. H. Dunstan.
Agricultural ammonia for stuck digesters.
In Proceedings; 20th Industrial
Waste Conference, Lafayette, Ind., May
4-6, 1965. Purdue University Engineering
Extension Series No. 118. p.126-130.
Methanogenic bacteria, which convert the
salts of volatile fatty acids to methane
and carbon dioxide during anaerobic
digestion, are inhibited by a decrease in
pH. Lime has been used to correct this
although it has been said that it favors
the formation of more volatile acids.
Agricultural ammonia (anhydrous ammonia)
has been used to restore pH since it is a
more efficient neutralizing agent and in
some areas is cheaper than lime. The
malfunction of a 2.0 mgd biofiltration
treatment plant at Pullman, Washington is
described and parameters of digestion are
listed. It was decided to add an amount of
anhydrous ammonia to neutralize the free
volatile acids and to have an effective
buffering alkalinity of 550 mg per liter
as calcium carbonate. The calculations
used to determine the correct amount of
anhydrous ammonia are given. Gas
production and the pH of the supernatant
increased, while the total volatile
organic acid content supernatant began to
decrease. Adding a calculated amount of
anhydrous ammonia based on meeting, the
deficit caused by the free volatile
organic acids in addition to giving a
working free buffering alkalinity of
500 to 1000 mg per liter as calcium
carbonate restored a distressed digestor
having a deficit in buffering alkalinity.
Buffering alkalinity of this magnitude
must be added to neutralize the free
volatile organic acids formed during
the lag and early growth phase of the
methanogenic microbiological population.
Anhydrous ammonia addition brought partial
relief to the distressed digestor in 5
days and complete recovery in 11 days.
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65-0433
Cooper, R. C., VI, J, Oswald, and J. C.
Bronson. Treatment of organic industrial
wastes by lagooning. In Proceedings;
20th Industrial Waste Conference, Lafayette,
Ind., May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.351-364.
Oxidation ponds or lagoons have been used
for the treatment of liquid industrial
wastes. Three types of ponds are discribed:
anaerobic, facultative, and aerobic. The
rendering plant waste treatment pond in
Woodland, California, is an anaerobic
lagoon which has handled both relatively
low and high organic loads effectively.
The petroleum refinery waste pond, a
144-acre lagoon designed and built to treat
wastes from an adjacent oil refinery,
treats many homologues of phenol,
partially oxidized water-soluble
hydrocarbons, and many oxidized sulfur
compounds. Data including BOD., color,
and bacteria are discussed. A number of
large poultry farms have successfully used
anaerobic lagoons for disposal of chicken
manure. Odors have frequently occurred in
using lagooning for cannery wastes.
Suggestions are given in regard to the
construction of ponds. The type of pond
selected will depend largely upon the
organic and hydraulic load anticipated.
65-0434
Culotta, J. M. Treatment of cyanide and
chromic acid plating wastes. Plating,
52(6):545-548, June 1965.
Three types of evaporation systems for
treating cyanide and chromic acid
plating wastes with consequent recovery of
the plating chemicals are described and
schematically illustrated. The three
systems are similar in that the plating
chemicals are recovered from overflow
from rinse tarks by evaporative
concentration of the solution. The
concentrated solution is returned to the
plating bath for reuse and distilled water
is recirculated to the rinse tanks.
Differences in the configuration of the
plating line and the type of plating
solution lead to variations in the typical
closed loop system which permits 100
percent recovery. In the open loop system
96 percent recovery is obtained, since
a minor part of the dragout overflow is not
reated bt the evaporative method. This
system has to be used when less than 3
rinse tanks are in line. The optimized
system recovers and purifies chromic acid
plating waste by evaporation and ion
exchange, while utilizing waste heat to
effect evaporation. Economic advantages of
the techniques are cited.
65-0435
Cundy, L. Industrial waste disposal.
Public Cleansing, 55(7):411-425 , July
1965.
Results and analysis of a questionnaire
sent to 21 British municipalities with
populations between 54,000 and 1,115,000
people, concerning their involvement in
disposal of industrial waste are
presented. Most cities offer at
least limited disposal facilities to
industry. Where more than one method of
disposal was offered, industry was required
to segregate it's waste for disposal by the
most convenient method. Many cities gave
no or only partial disposal service or
dangerous wastes. The central government
should of necessity take control and
establish a code for municipalities and
industry to follow. It was recommended
that local authorities offer, at industry's
expense, complete disposal service for small
waste producers, and incinerator ash landfill
space for waste producers arge enough to
operate their own incinerators. Research
programs on disposal methods, and regional
approaches to disposal should be initiated
on a municipal-industry basis. A
discussion of the paper followed.
65-0436
Davies, A. J. Public abattoir at
Withybush, near Haverfordwest. Surveyor
and Municipal Engineer, 125 (379):25-27,
Mar. 27, 1965.
The description of the public abattoir
at Withybush near Haverfordwest includes
a description of the waste disposal
system which will discharge a fully treated
effluent to an adjacent stream. The
pictures in the article shov a west elevation
of the abattoir, a sketch of a side view,
the lairage, the beastrails and carcase saw,
a ground floor plan, the sheep rails and
stunning pen, but no pictures of the
waste treating operations. The abattoir
wastes and, especially the blood, have a
high BOD. The discharge is estimated
at 8,000 gal per day discharging in 4
hr. The liquid flow through the upward
settling tank and humus tank has been
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Industrial Wastes
kept down to 1 ft per hr in the 18-ft
square hopper bottom tanks. Normally the
flow would be 3 ft per hr. With a 30-ft
diameter filter, the flow through the
filter was 50 gal per cu yd per day. The
sludge beds cover 360 sq yd. The effluent
passes from the humus tanks to retention
tanks with a capacity of 8,000 gal. This
material is recirculated to the dosir-.r
syi'1-'^ so that the effluent will pass
through the filter and humus tank at
least three times before discharge.
The blood and stomach contents go
directly to the sludge beds, the liquor
of which is returned for treatment.
This results in the blood coagulating
on the beds, therefore desludging is
necessary at frequent intervals, possibly
twice a day. If the blood could be
disposed of as a by-product, it could
be stored in a blood storage tank. The
cost of the sewage works was B10.709 out
of a total cost of the abattoir of h52,007.
650437
Davis, R. V., C. E. Cooley, an<5 A.
W. Hadder. Treatment of duck wastes and
their effects on the water quality in the
Rappahannock River, Urbanna, Virginia. In
Proceedings; 20th Industrial Waste
Conference. Lafayette, Ind., May 4-6, 1965.
Purdue University Engineering Extension
Series No. 118. p.626-646.
Two duck farms, about 2.5 miles apart,
have been discharging wastes into the
Rappahannock River for the last 30
years. A map shows the location which is
near Chesapeake Bay in waters used
extensively for oyster production and
recreation. It was estimated that
treatment costs might be $.08 per duck or
an annual cost of $46,000. The operation
of the farms is described. The water
for the flowing stream is pumped from
deep wells and the ducks have access to
it for 4 weeks. The waste problem is
generated solely by the ducks during the
period on the runs. The feathers, viscera,
and feet are marketed as products and
slaughtering and processing contribute
little to the waste problem. Laboratory
studies were carried out. Then samples
were collected from six different
locations and placed in six open plastic
tanks (20 in. by 16 in. by 16 ft) to a depth
of 14 in. Hourly samples were collected
for the first 5 hr and daily for 20 days.
Each sample was analyzed for BOD., solids,
and coliform organisms. A marked
reduction of coliform and BOD. was
found at the end of 3 days and at the
end of the fourth day the coliform organisms
had been reduced about 93 percent. The
optimum settling time for the samples was
between 1.5 and 2 hr. Chlorine residuals
(5-15 mg per liter) had no effect on the
settling wastes. Lagooning was suggested
as a method of treatment and a test lagoon
(12 by 14 by 4 ft) was dug, filled with
about 5,000 gal of raw waste and allowed
to stand. The results obtained were not
reliable because a tear in the plastic
material allowed a daily seepage of about
1,000 gal.
65-0438
Dewatering of sludge. Water and Waste
Treatment, 10(7):361-362 , May-June 1965.
A summary is given of a paper presented
by J. D. Swanwick and P. C. Baskerville at
the London International Engineering
Exhibition. Various aspects of dewatering
of sludge by drying beds are discussed.
The scarcity and cost of labor for manual
lifting of sludge has been alleviated by
the mechanization of beds. Benefits can
also be derived from elutriation of the
sludge, particularly when it is characterized
by slow-draining and high specific
resistance. Various depths of application
of sludge between 4 and 12 in. have been
used and the results suggest that the
solids loading may be a more suitable
parameter than hydraulic loading. The
use of opaque covers has been known to
reduce bed performance in summer months. The
filtration characteristics of both crude
and digested sludges were studied at
various sewage works. It was concluded that
basic data have been obtained on dewatering
sewage sludges on beds both to a life
table state and to a solids content of 40
percent.
65-0439
Disposal of sludges. Water and Waste
Treatment, 10(7) :361, May-June 1965.
The comments of Mr. V. H. Lewin at the
Effluent and Water Treatment Convention
are summarized. The sludge disposal
problem is too frequently bypassed by the
'temporary' adoption of dumping, a cheap
alternative, but of limited duration. Where
sludges are nontoxic, the most economical
method of disposal is consolidation
and distribution to agriculture. Where
agricultural use must be ruled out because
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0437-0442
of toxic content, further dewatering, even
combustion to a fine ash, may be necessary.
Under certain conditions, heat treatment
might extend the usefulness of disposal to
agriculture by rendering the material
sterile and might also act as an aid to
concentration of activated sludge. More
needs to be known, through research, of
such factors as costs, liquor effects, the
foam question, and the differences apparent
with varying qualities of sludge. In
addition, there is a need for properly
supervised dumping facilities on a national
or reeional basis.
65-0440
Doe. P. W., D. Eenn, and L. R. Bays.
Sludge concentration by freezing. Water
and Sewage Works, 112(11) :401-406 , Nov.
1965.
The development of a process for
waterworks sludge concentration by slow
stirring to pre-thicken and then freezing
is described. A full-size pilot plant
was designed and build for a freezing and
thawing cycle, which consists of an
exchange of heat between frozen and thawed
sludge. A detailed study of the plant
showed that the tanks fatigued under the
stresses caused by continual freezing and
thawing. A duplicate plant was built with
improved design which has a rated output
of 8,500 gpd at the maximum economical output.
The sludge freezing plant-stocks filtration
plant and a part-sectioned sketch of the
sludge freezing tank are schematically
illustrated. The fundamental features of
the process include: (1) raw sludge which
can be collected and pre-thickened, using
either mechanical means or further
coagulation; (2) storage tanks to even-out
input variations and give additional
thickening; (3) a 'batch' process to
recover latent heat; (4) a complete and
slow freeze for the production of hard
solids and supernatant water on thawing;
and (5) tanks capable of withstanding the
heavy and continual stresses caused by
repetitive freezing and thawing. One
thousand, six hundred fifty Ib of solids per
day are abstracted from 33,000 gal of
bulky colloidal sludge, leaving the
supernatant water to run to the river.
The solids accumulate in a small area about
one-eighth the size of that previously
necessary for untreated sludge, and when
this space is full it can be covered with
soil and planted with grass. The total
capital outlay of the plant was i63,000
with operating costs varying between fc2.42
and L3.39 per 1,000 gal of sludge.
65-0441
Dyck, A. W. How CZC pulps sawdust in a
continuous digester. Paper Industry,
47(8):44-45, Aug. 1965.
The 150 tpd capacity American Defibrator
continuous digester for sawdust pulping,
which was installed at a mill in Canada
early in 1964, is described. Sawdust is
unloaded from barges with a Colby crane
and carried by belt conveyor to a blower
system which delivers it to two 22
unit per hr capacity Rotex 522 screens.
The screened sawdust is blown to a
360-unit concrete silo equipped with
a 12-ft diameter Link-Belt turntable
feeder, which moves it to a belt
conveyor. It then travels to a blower
and to the digester bin, which has two
cone-shaped outlets to supply the twin
feed-lines of the digester. Two
metering screws supply sawdust from the
bin outlets into two stainless steel
wetting tubes with cooking liquor
introduced through cyclones into the top
sides. The wet sawdust passes into a
high pressure feeder which delivers it
by conveyor to the first digester tube.
Three digester tubes are each equipped with
a screw conveyor driven by a 25 hp motor
at speeds between 1.5 and 6 rpm with pressure
in the cross conveyor and digester tubes
maintained at 150 psi, cooking temperature
at 342 F, and retention time 30 to 45
minute. The cooked sawdust then passes
through a blow tank and a Selectifier screen,
and is subsequently washed in three
stages and bleached in five stages. Two
recovery furnaces operated by the mill, which
together generate 500,000 Ib of 600 psi
steam per hr, are described. A second
scrubbing system, designed for pulp mill
odor control, is also described.
65-0442
Engineering in Wales--find the bugs.
Engineer, 199(5160):321-322, Mar. 12,
1965.
Government DSIR grants totaling 631,420
have been given to the microbiology,
mechanical engineering, and physics
departments of two universities for a
program of biological engineering
research on the treatment of effluents
and the control of corrosion in containers
for fuel oil, cleaning, and cutting
fluids. The first group of experiments
will study methods for removing the tons
of bacteria and associated solid material
from the millions of gallons of water
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Industrial Hastes
handled in town sewage and industrial
Waste disposal. Wastes from the coal
•and oil fuel industries, chemical plants,
and paper making will also be studied.
The second group of experiments will be
concerned with growth, survival, and
activity of micro-organisms in non-aqueous
media such as petroleum fuel oils,
cleaning and cutting fluids. It appears
that micro-organisms can spoil or modify
such fluids, with resultant damage to
containers. It may be possible to turn
this activity into a useful channel by
making waste products usable, Experiments
on capillary flow will be used as a
basis for attempting to develop irethods of
concentrating and more efficiently removing
solids suspended in effluents, with the
hope that the work will lead to an
industrial pilot plant. Collaboration
between the physicist, engineer, and
biologist may make possible the teaching
of biology to graduate engineers froir1
industry.
65-0443
Evans, R. , K. Baumann, and F. Lewis.
Sludge handling practices as related to
.anaerobic digesters. Water and Sewage
Works, 112(4):135-138, Apr. 1965.
The results of a general study of digesters
operating in 13 municipalities for the
primary purpose of gathering information
on everyday operating conditions, are
reported. The feed sludges were analyzed
and the average temperature, total solids,
volatile solids, pH, and the volume handled
by the digesters are reported. The
mechanism of sludge digestion was reviewed.
Since the organic acid-alkalinity balance is
probably the most important factor in
proper digestion processes, the amount of
organic acids and the alkalinity (mg/1 as
calcium carbonate) in the fed sludge and
digester sludge was determined and
illustrated graphically. Without artificial
agitation of digester contents, and within
the temperature range of 92 to 98 F,
a 30-day detention period is considered
adequate for the reduction of volatile
matter in normal domestic sludges. With
agitation, thus increasing contact, and
at optimum temperature, proper volatile
matter destruction can be accomplished in
15 days or less. Tabulated data presents
the displacement: time and gas production
observed during the study. It is
emphasized that preliminary investigation
indicates that the biological state of
digestion might be characterized by the
relative concentrations of acetic, propionic,
and butyric acids. The systematic study
of digesters, and subsequent preparation
of case histories by the managers of
sewage treatment works, will help develop
tested control practices that can be applied
in correcting a malfunctioning digestive
process or sustaining a productive one.
65-0444
Ferber, M. Amount and composition of
liquid waste. In Refuse and waste disposal.
Berlin, Druckhaus Lichterfeld GmbH, 1964.
The amount and composition of domestic
sewage and trade and industrial sewage are
discussed. The amount of domestic sewage
roughly corresponds to the consumption
of water. The composition of the sewage
is important for planning a sewage
treatment plant. Daily fluctuations in
sewage are discussed. The quantity of
trade and industrial sewage can be
estimated from water consumption if large
amounts do not evaporate. Its composition
cannot be described by average values
because production processes are too
variegated. For dimensioning sewage
clarification plants and allocating the
corresponding operating costs, the sewage
pollution is expressed in inhabitant
equivalents.
65-0445
Finstein, M. S., and H. Heuelekian.
Filamentous micro-organisms and the
bulking of activated sludge. In
Proceedings; 20th Industrial Waste
Conference, Lafayette, Ind., May 4-6,
1965. Purdue University Engineering
Extension Series No. 118. p.175-181.
Aeration tank mixed liquors from four
activated sludge sewage treatment plants
were examined to provide quantitative
data to assess the influence of
filamentous microorganisms on the
settleability of activated sludges. One
of the four plants operates with a mixed
liquor suspended solids concentration of
about 1 ,300 mg per liter and a detention
time of 1.5 hr. The others are
conventional plants with detention time of
about 6 hr. Floes were characterized
with respect to their diameters and the
total length of associated filamentous
microorganisms per flox. Floes generally
range from 0.02 to 0.2 mm in diameter.
The total length of filaments per floe
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0443-0447
ranged from 0 to about 2.0 mm. In any
given sample the population of floes
was extremely heterogeneous with respect
to the characteristics measured. No
consistent relationship was found between
floe diameter and sludge volume index
(SVI) . Of samples taken from a specific
treatment plant at different times, the
more filamentous sample always add the
higher SVI. SVI was also, at two plants,
related to the mean total length of
filaments per floe by a constant factor.
Because of this evidence it is inferred
that filaments govern SVI to a large
extent.
65-0446
Flower, W. A. Spray irrigation - a
positive approach to a perplexing problem.
In Proceedings; 20th Industrial Waste
Conference, Lafayette, Ind., May 4-6, 1965.
Purdue University Engineering Extension
Series No. 118. 'p.679-683.
The Howard Paper Mills of Urbana, Ohio,
seeking treatment of its industrial
waste, would provide 85 percent BOD.
reduction, would be economical, and would
be free of nuisance conditions, considered
the use of spray irrigation, although
the numerous pitfalls and large expenditure
of money were detracting factors. In
order to determine the feasibility
of using spray irrigation for waste
disposal, a pilot project was set up
which investigated; (1) What cover crop
was most suitable0 (2) How much land
would be required? (3) How much attention
would it need? (4) How much water could
be applied9 (5) What is the tolerance
of the cover crop to waste materials? (6)
Would ground water become polluted?
and (7) How to dispose of the cover crop
when harvested? The permeability of the
soil was determined. Alfalfa was selected
because it has a particularly high
transpiration rate, has a massive root
structure, and withstands the stress
of sprinkling. The fine-bladed grasses
such as orchard or bent grasses were
found to serve as excellent cover crops,
requiring less care, although offering no
economic return. The alfalfa was
completely destroyed at the end of 5 days
(20 in. of water), indicating the need
for constant attention in operating a
spray irrigation system. Testing under
cold weather conditions confirmed that
spray irrigation is strictly a warm-to
moderate-temperature operation. Sampling
of test wells indicated no correlation
between the well water and the waste
applied, with the exception of BOD.
Based on the experience cf the pilot
plant, full-scale operation of a 117-acre
spray irrigation system providing 100
percent treatment of wastes from the mill
will begin.
65-0447
Follett, R. H. Plastic trickling
filter--activated sludge treatment of
paper wastes. In Proceedings; 20th
Industrial Waste Conference, Lafayette,
Ind., May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.120-125. '
A combination of a roughing plastic media
trickling filter and activated sludge
process was tested as a method of
secondary biological treatment. The
pilot plant was operated over a 2 year
period, treating settled effluent from
a fine papermill, boardmill, and a papermill
employing deinking. The pilot plant was
operated with each waste, first as an
activated sludge unit alone and, when its
performance was determined, at increasing
loading levels. The return sludge and
the feed were switched to the filter
starting at a low rate of application.
Graphs show: series trickling filter
treatment, activated sludge verus
combined treatment of fine papermill
waste, activated sludge versus
combined treatment of deinking papermill
waste, and combined treatment of
boardmill waste. Capital cost comparisons
were made of the two systems, and the
data indicate that combined treatment
plants can be built at from 5 to 25
percent less than the cost of activated
sludge plants. Besides better performance
and reduced cost the combination system
improved the settleability of the
activated sludge while treating fine
papermill effluent. The trickling filter
can be used as a cooling tower to cool
hot waste to be treated by_ the activated
sludge unit. The amount of activated
sludge produced was about the same for
the two treatment methods, (generally
0.5 Ib dry solids per Ib of BOD. removed)
with the same dewatering characteristics.
Recirculation of activated sludge to the
trickling filter increased the efficiency
of the unit. The greatest advantage of
the combined system is the uniformity
of performance at high loading rates.
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Industrial Wastes
65-0448
Goodman, B. L., and C. P. Witcher.
Polymer-aided sludge elutrlation and
filtration. Journal of the Water
Pollution Control Federation,
37(12) :1643-1656, Dec. 1965.
Despite past failures, the elutriation
system is being made to function
properly in Ann Arbor, Michigan, to
remedy present sludge disposal problems.
Single-stage elutriation must be
employed to reduce the concentration of
sludge alkalinity. This sort of dilution
is either fill and draw or continuous.
Sludge can also be taken through a
multistage operation or elutriation can
be carried out in two steps in which the
recovered wash water from the second
step is returned for reuse in the first
step. Addition of alum proved ineffective
for countercurrent elutriation units.
Because of individual sludge variations,
no specific elutriation system design
criteria is possible. Ann Arbor studies
revealed that utilising cationic, synthetic
polymers of hi^h molecular weight could
overcome expected shifts in the efficiency
of properly designed units. Tests of
various polymers were undertaken and
results plotted as percent recovery of
wash water vs. time. As data show,
different polymers were best for different
needs. Reten 205M, for example, improves
the sludge's settling characteristics
and increases the unit efficiency at a
variety of elutriation ratios. To date,
no basis has been established for
predicting the effectiveness of a particular
polymer for conditioning a particular sludge.
Generally, sludges which can be
conditioned easily with conventional
inorganic coagulants also can be
conditioned easily and cheaply x-dth
polymers. It also appears that
polymer-conditioned sludge can only
be dewatered with top- loading filters.
Various synthetic polymers aid in sludge
conditioning, elutriation, sludge index
control, and pressure flotation.
65-0449
Grieves, R. B., K. Y. Shih, T. E. Wilson,
et al. Ion flotation for industrial
wastes: separation of hexavalent
chromium. In Proceedings; 20th Industrial
Waste Conference, Purdue University,
Lafayette, Ind., May 4-6, 1965.
Purdue University Engineering Extension
Series No. 118. p.110-119.
Ion flotation, which involves the
formation of a surface-active complex by
means of the addition of a surface-active
ion of opposite charge to separated,
has been employed for the removal of
organic anions and cations from aqueous
solution. The complex is floated to the
surface by generated gas bubbles. If
the complex is soluble it may be termed
foam separation. If the complex is insoluble
and is floated from solution in the form
of colloidal-size particulates, the process
may be termed ion flotation. The
feasibility of ion flotation for the
separation of hexavalent chromium from
aqueous solution, using a cationic
surfactant which forms an insoluble
complex with dichromate iron, was
investigated. Batch and continuous flow
experiments were included, with major
emphasis placed upon the effects of
dichromate concentration and surfactant
concentration. In both sets of experiments,
the addition of the ethylhexadecyldimethylammonium
bromide to the potassium dichromate
solution produced a distinct cloudiness,
indicating the formation of fine, colloidal
particulates consisting of complexed
dichromate and EHDA ion. A second set
of batch experiments was conducted to
determine the influence of pH upon the
ion flotation of dichromate and to
establish any interference that other
anions might have upon the removal of
dichromate. Based on the limited number
of experiments; the ion flotation of
dichromate appears to be feasible for
the separation and concentration of
hexavalent chromium from aqueous
solutions. With batch operation, lower
residuals of dichromate and of surfactant
were obtained than with continuous
operation; however, the pulsed feed of
surfactant which was used would be
analogous to multicolumn operation on a
continuous basis.
65-0450
Grune, W. N. Automation of sludge digester
operation. Part 1. Journal of the
Water Pollution Control Federation,
37(3):353-380, Mar. 1965.
It was shown that sludge disposal
construction costs range from 25 to 54
percent of the total treatment plant
investment. As research studies become
more complex while funds remain limited,
it appears automation will become more
important in the future. Three new
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044« 0452
parameters were studied to improve
the control of sludge digestion.
Anaerobic process automation by
oxidation-reduction potential, liquid
conductivity, and gas chromatography
appears feasible. These new methods were
employed to measure the eases given off
to the atmosphere, the liquids which
ultimately enter the stream, and the
solids which are returned to the soil.
The following results were obtained:
Redox-potential can be used to measure
the emf of the system for long periods
of time; trends in redox-potential are
reproducible; and there exists a direct
relationship between redox-potential and
cumulative gas production. Liquid
conductivity allows much to be predicted
about the state of sludge and there is a
correlation between conductivity, total
solids, and the degree of composition of
a sludge mixture. Gas chromatography can
continuously analyze each of the
components present in sludge digestion
gas, and be interpreted by the 'peak
height fraction' method when a liquid
partition column is used. It was found
by the gas chromatographv method that
the carbon dioxide concentration was 30
percent or less by volume and that neither
hydrogen or hvdrogen sulfide x-jas found
in the seeded sludge mixtures. The
need for new and better systems exists
and such systems are in various stages of
deve] opment,
65-0451
Hanes, B. N., G. A. Delaney, and C. J.
O'Leary. Pelationship between Escherichia
Coli, type I, coliform and enterococci
in water. In Proceedings; 20th
Industrial Waste Conference, Lafayette,
Ind., May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.210-219.
The most satisfactory method for bacterial
evaluation of water is to use an
indicator organism. The two kinds of
bacteria found in fecal material that
may be used as indicators are the
coliform and the enterococci groups.
Although the coli form group has many
advantages as an indicator, their ubiquitous
nature prevents their indicating fecal
contamination, and they may even multiply
in water. Although the enterococci group
have been of little use because of the
difficultv in testing and their small
numbers in sewage, the recent use of
sodium azide as an inhibitor has
developed a simple test for them. Graphs
show: the logarithmic deatii phase for
two indicator bacteria; survival curves
for coliform and Escherichia coll, type
I, the relationship between coliform and
enterococci; and the relationship between
Escherichia coli, type 1, and enterococci.
Although many authors have concluded that
the presence of either enterococci or E.
coll, type I, in water indicates fecal
contamination, they are present in animal
feces exposed to streams; therefore the
presence of these bacteria will not
indicate a dangerous public health, condition.
A definite equation cannot be developed
for the relationship between enterococci
and the c^liform group or E. coli, tvpe I,
because the relationship will var> wit'..
the source of contamination. A graphical
relationship between E. coli , tvpe T,
and enterococci mav be use.d to differentiate
between human fecal contamination and
fecal contamination of other warm blooded
animals in stream water.
65-0452
Hann, R. W., and F. D. Callcott. A
comprehensive survey of industrial waste
pollution in South Carolina. In
Proceedings; 20th Industrial Waste
Conference, Lafayette, Ind., May 4-6,
1965. Purdue University Engineering
Extension Series No. 118. p.538-550.
The three major phases of the study were:
locating the industries and getting
basic information about then; studying
the specific industrial processes through
questionnaires and visits; and cataloging
the present waste treatment facilities
and evaluating industrial waste loading.
The textile industry is of paramount
Importance: one-third of the country's
textile spinning and weaving and 50
percent of the country's textile finishing
is done in South Carolina. Other
significant industrial groups are: the
pulp and paper industry, food processing,
and metal plating. A cotton weaving (low
diagram is given. The distribution of
grey goods producers throughout the
state is shown on a map. Similar figures
are given for textile finishing, wool
processing, and paper making. A map
showing the treated and untreated
effluents from textile finishing is
presented. The present status of
waste disposal for each industry is
summarized. The population equivalents for
11 river basins are given for the major
industrial groups of teytile, pulp and
paper, food processing, and electroplating.
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Industrial Wastes
The total population equivalent is
4,576,300.
65-0453
Hanna, G. P., W. D. Sheets, P. J. Weaver,
et al. A field study of LAS biodegradation
by modified activated sludge. In
Proceedings; 20th Industrial aste Conference,
Lafayette, Incl., May 4-6, 1965. Purdue
University Engineering Extension Series
Mo. 118. p.725-734.
A 16-month study sponsored by the Proctor
and Gamble Co. at Ohio State University
has confirmed the biodegradability of
the new linear alkyl sulfonate (LAS)
and its biodeg.radability was compared to
that of alkyl benzene sulfonate-(ABS)
based products now being replaced by LAS.
The test site consisted of 88 homes.
Each home was provided with detergent
formulations of known composition. The
original treatment plant utilizes a
modified activated-sludge or extended
aeration type of treatment. The receiving
stream is variable in flow. Sigma pump
units were used for automatic collecting
raw influent and final effluent samples.
The main operational variables considered
were type of surfactant, variation in
aeration time and mixed liquor suspended
solids. The program was divided into 3
major parts: operation with home owners'
normal purchase product, a test of ABS
biodegradability, and a test of LAS
biodegradability. In each of the tests,
attempts were made to vary the condition
so that the biodegradability at different
aeration times in mixed liquor
suspended solids levels would be obtained.
LAS was found to be much improved in
biodegradability over ABS for all
comparable operating conditions. The
efficiency of removal of LAS is
proportional to the contact time in the
aeration tank. LAS shows an acclimatization
to aerobic digestion, and an increase in (
degradability with a corresponding
increase in detention time and mixed
liquor suspended solids. LAS removals
appear to be better than overall BOD and
COD removals, and under conditions w-ten
the plant was operating efficiently and
after acclimatization were comparable to
soluble BOD removals.
65-0454
Harding, J. C., and G. E. Griffin. Sludge
disposal by wet air oxidation at a five
MGD plant. Journal of the Water
Pollution Control Federation, 37(8):1134-1141 ,
Aug. 1965.
The modernizing project at the Blind
Brook District plant, Rye, New York, was
to adapt it to wet air oxidation of sludge.
Wet air oxidation is a process in which
oxygen in air, under greater-than-atmospheric
pressure, combines with organic material
in aqueous solution or suspension below
the critical temperature (372 C) at
which water ceases to be in a liquid
phase. The modernized project consists
essentially of: (1) a disintegrator to
reduce particle size; (2) a storage
tank for preliminary heating; (3) a steam
generator to furnish start-up heat; (4)
a centrifical pump for transfer
of sludge from the storage tank; (5) a
high-pressure pump to increase the
pressure for the heat excfhangers; (6)
an internal diam reactor; (7) a
separator which separates gaseous products
from the liquid and solid portions of the
reaction product; (8) a diffuser or
perforated bottle to mix vapor-phase
products with the wastewater flow; (9)
pressure-reducing valves and liquid-level
controllers; and (10) an ash-separation
tank in which the solids portion of
the residue is settled and from which the
ash is discharged to a drainage bed. Air
at the required pressure is supplied
by a three-stage reciprocating compressor.
An instrument panel monitors all operating
data, It was found that operation of the
unit was necessary only on 4 or 5 days
of alternate weeks. This process is an
economical and appealing solution of the
sludge-handling problem for small plants.
Additional operating data is contained
in this report.
65-0455
Hetling, L. J., and D. R. Washington.
Kinetics of the steady-state bacterial
culture III. Growing rate. In
proceedings; 20th Industrial Waste
Conference, Lafayette, Inc., May 4-6,
1965. Purdue University Engineering
Extension Series No. 118. p.254-264.
The relationship between the rate of
growth of the microorganism and the
substrate concentration in the system
is one of the more important relationships
in the design of a biochemical waste
treatment process. The literature shows
that both biologists and engineers
disagree on this relationship. The
110
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0453-0458
purpose of this research was to determine
under laboratory conditions the
relationship of substrate concentration
to growth rate where the substrate
concentration is measured as COD. An
open, homogeneous, continuous culture-
apparatus was constructed and operated
under various growth conditions using
different organisms and substrates.
Pure cultures of bacteria were used to
maintain a steady-state. The continous
culture, completely mixed, activated-
sludge system in its simplest form
consists of a reaction vessel to which
medium with a fixed substrate concentration
is added at a constant flow rate and with
a constant volume. The temperature, pH,
pressure, and other environmental
conditions were considered to be constant.
Graphs show the effect of dilution rate
of dissolved COD using various substrates.
The effective growth rate was found to be
equal to the dilution rate. Although the
data indicated that the constants involved
are unique to each combination of substrate
and organism, the general relationships
apply to any predominantly microbacterial
process. For an industrial waste treatment
process the constants would be different for
each waste.
Waste disposal investigators of the
Pennsylvania Mines and Mineral Industries
Department have been instructed to enforce
a 1956 State Act which provides for the
regulation of refuse disposal areas in the
anthracite and bituminous coal regions
in order to prevent the ignition of fires.
The sections will be surveyed to determine
that permits have been issued to cover
all areas where rubbish is being dumped. It
is thought that the major portion of the
mine and refuse bank fires now burning in
these coal regions may have been started
by the ignition of refuse dunped in the
areas. These fires are annoying to nearby
residents, as well as costly to extinguish.
Notices will be posted on land not licensed
and where trash is being dumped, indicating
that the spot is not a licensed waste
disposal area. Mine inspectors are to
observe refuse disposal areas in their
districts and to report infractions.
Any person or property owner using land
as a waste disposal area without a
permit will be reported and will be
subject to prosecution.
65-0456
Hurwitz, E., G. H. Teletzke, and W. B.
Gitchel. Wet air oxidation of sewage
sludge. Water and Sewage Works, 112(8):
298-305, Aug. 1965.
The characteristics of several sludges
oxidized to various degrees are reported.
Solids from low degree as well as high
degree oxidations exhibit qualities such
as sterility, biological stability,
settleability, and drainability which
make the end products suitable for
ultimate disposal. The choice of degree
of oxidation will, therefore, depend on
consideration of factors specific to the
local situation such as the size of the
plant, availability of land for ultimate
disposal, power costs, etc. The wet air
oxidation process offers a wide selection
of end products and disposal process now
available. The relationships of COD
reduction to temperature, insoluble
organic reduction, volatile solids,
settled oxidized solids, and BOD.
exertion are graphically illustrated.
65-0457
Illegal dumping cause of coal mine fires.
Refuse Removal Journal, 8(1):14, Jan. 1965.
65-0458
Industrial solid waste disposal practices
in England. Public Works, 96(9):66,
Sept. 1965.
Questionnaires concerning problems and
methods for industrial solid waste disposal
were sent to 21 local authorities in
England and replies received from 18 of
them. Eight said that their authority
offers facilities to industry for the
disposal of its wastes; nine said they
did, with qualifications; one said it
did not. As to the methods employed,
eight provided controlled tipping and six
used a combination of controlled tipping
and incineration. In regard to
contemplated changes, eight did not plan
any changes; eight were considering the
provision of further facilities, including
separation and incineration, pulverizing,
or composting. Dangerous or difficult
substances were not accepted by five of the
respondents; seven reported limited
acceptances; and six had no limitations.
As to quantity or tonnage, three kept no
records; the others reported amounts ranging
from 2,000 to 57,000 tons annually.
Other replies indicated that industry also
disposed of wastes privately and that the
method, where known, was mainly tipping.
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Industrial Hasten
65-0459
Industrial waste collection at West
Bromwich. Public Cleansing, 55(5) : 282-286 ,
May 1965.
West Bromwich, England, has instituted
a municipally-controlled industrial waste
disposal system utilizing the Dempster
system. Many municipalities require
industry to dispose of their own wastes,
which is usually done by open burning
or open dumping. By renting the containers
at $2 per week and charging $7 per visit
for refuse removal, the system supports
itslef, ad, a]lows the municipality to
control the place and manner of dumping.
Sixty 8-yd containers are in use, and
two dumpsters empty all but five1 of the
containers on a daily basis.
65-0460
Jensen, C. L. Industrial wastes from
seafood plants in the state of Alaska.
In Proceedings; 20th Industrial Waste
Conference, Lafayette, Ind., May 4-6,
1965. Purdue University Engineering
Extension Series No. 118. p.329-350.
The wastes from the seafood plants in
Alaska in 1964 were: salmon, 103 million
Ib; king crab, 69.5 million Ib;
dungeness, 10 million Ib; shrimp, 5.5
million Ib; and halibut, 3.4 million
Ib, This cost the processors over $21
million, A 4-year average of costs was
$16 per year. Fish meal made of herring,
anchovies, tuna offal, and menhaden is
sold for $130 to $160 a ton. Although
king crab waste contains calcium, iron,
magnesium, manganese, zinc, and copper
(all essential for good crops), it contains
little protein. The other elements could
be used in the fertilizer industry. The
salmon industry spends almost $48
million for its raw material and throws
away 30 percent as waste. The vast
amounts of fishery wastes (190 million
Ib in 1964) shoxild be of interest to the
fish meal industry. These wastes are
being dumped in Alaskan waters and are
a potentially dangerous pollution problem.
The wastes are particularly dangerous to
the shellfish industry which requires
relatively pure salt water for live
tanking purposes. The paramount problem
is the great distances between primary
production points. At the primary
plant a storage system would have to
be provided to handle the day-to-day
production of .jaste which would later be
collected by barges capable of carrying
several tons. Primary reduction units
might be installed at the primary source of
raw material. Primary drying and dry
storage might lead to a problem of spontaneous
combustion. The waste might be reduced
chemically to a thick type of slurry which
could be stored for pumping into the
barges.
65-0461
Jones, P. H. The effect of nitrogen
and phosphorus compounds on one of the
micro-organisms responsible for sludge
bulking. In Proceedings; 20th Industrial
Waste Conference, Lafayette, Ind.,
May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.297-315.
Evidence is offered that a variety of
filamentous microorganisms are intimately
associated with the sludge bulking
phenomenon. Mixed liquor was obtained
from a sewage treatment plant in Chicago
and was fed a synthetic sewage rich in
carbohydrates. The equipment consisted
of 4 liter aspirator bottles with magnetic
stirrers and magnets. The cultures were
aerated and the temperature measured. The
effect on growth rate of a cross-section
of organic and inorganic nitrogen sources
when combined with a series of different
carbon sources was studied. Experiments
were designed to study the effect of
nitrogen deficiency on the growth rate
of Geotrichum and at what concentration of
nitrogen (BOD/N) this nutrient became
the limiting factor. These experiments
were done in three series; in each series
a single nitrogen source was considered
and the BOD/N ratio was varied from
25 per liter down to 500 per liter. The
effect of higher BOD per P ratios on the
specific growth rate was yielded by the
organic nitrogen sources, peptone and
hydrolyzed casein and the lowest growth
rate by nitrate nitrogen. From these
experiments it was noted that the effect
of the nitrogen source is also related to
the carbon source available. A second
series of tests using the anionic
synthetic detergent, alkyl benzene
sulphonate, and the non ionic synthetic
detergent 'Energetic' is reported.
A BOD per P ratio of 100 is the maximum
tolerable for activated sludge. It: was
deduced that in phosphorus or nitrogen
deficient wastes Geotrichum has an
advantage over other microorganisms.
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0459-0464
65-0462
Jones, P. H. Waste treatment in the urban
society. Canadian Medical Association
Journal, 93:26-32, July 3, 1965.
In order to reuse water which has been
used as a vehicle for wastes in sewers,
it is necessary to remove the wastes
from the water. This review discusses
the functions of the modern sewage
treatment plant. Wastes are treated for
two distinct purposes; to separate water
from putrescible organic material, both
dissolved and particulate and to disinfect
the water to prevent the transmission of
water-borne pathogens. The separation of
solids is accomplished by flocculation
followed by settling. The flocculation may
be induced biologically or chemically,
with the former method the more economical
where practical. The methods of
bioflocculation described include the
following: activated sludge, contact
stabilization, tapered aeration, step
aeration, total oxidation, and trickling
filter. The non-mechanical methods of
sewage treatment are economically and
technically sound in areas where the
sewage flow is small and the land costs
are low, as is the case in many rural
applications. The lagoon or oxidation
pond resembles the total-oxidation or
extended aeration method except that the
air used is that dissolved from the
atmosphere. In Ontario, regulations
require that sewage be detained in the
oxidation pond for 80 to 100 days before
release to the receiving stream. The
choice of a method for waste treatment must
be based on the type of waste to be
treated, the fluctuation in waste quality
and quantity, the degree of treatment
required, and the relative economics of
the methods considered.
65-0463
Joyce, R. S., and V. A. Sukenik.
Feasibility of granular, activated-carbon
adsorption for waste-water renovation.
In Environmental health series, water
supply and pollution control. AWTR-15.
[Washington], U.S. Department of Health,
Education, and Welfare, Oct. 1965.
p.1-38.
Granular, activated carbon in packed-bed
column contactors 20 ft deep and operated
at a flow rate of 4 gpm per sq ft reduced
the COD to an average value of 18.5 ppm.
The removal was not significantly different
from the removal obtained when operating
the sfnie column at 10 gpm per sq ft.
After 4 months of operation, the first
quarter of the column length was still
accomplishing a significant part of the
overall removal. Typical adsorption
isotherms for type SGL carbon for COD
indicated capacities of approximately 35
percent by weight. The cyclic saturation
and regeneration of activated carbon
through 16 cycles had an average carbon
loss of 4,6 percent per cycle. A practical
adsorption capacity was maintained for the
regenerated carbon even though reactivation
conditions for carbon spent on municipal
waste-water treatment purification have not
been explored and optimized. Flocculation
with alum of secondary effluent prior to
carbon adsorption increased the adsorption
capacity of the carbon and resulted in
much lower final levels of COD than the
levels obtained with unflocculated
effluent. The report includes explanatory
tables and figures.
650464
Kershaw. M. A. Development in sludge
treatment and disposal at the Maple Lodge
Works, England. Journal of the Water
Pollution Control Federation, 37(5):674-691 ,
May 1965.
Sludge treatment and disposal present an
entirely different problem from disposal
of sewage effluent. This paper deals
with the work of the 'vest Hertfordshire
Main Authority in the field of sludge
disposal. The main treatment plant
rests over a large reservoir of underground
water, causing some problems. Following
a visit to America, it was decided
to install a heat treatment and vacuum
filtration system, the only flash-drying
plant in England. This system was not
adequate to handle all the sludge which
entered the plant and sludge treated
did not justify operating costs. Excess
liquid digested sludge is transported
by tanker trucks to local farmers without
charge for use as a soil builder.
Sludge drying beds looked to be the best
solution, hut labor shortage was a
problem, thus the beds were installed with a
nearly completely automated system of
handling. It has mechanical gear for
lifting, a conveyor system for transporting,
and a stockpile area. Charts eive the
cost and production of sludge and
rainfall. A detailed description
of sludge drving facilities is piven.
These sludge beds have operated successfully
for the first vear of operation.
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Industrial Wastes
Though more expensive, the drying method
provides a more satisfactory means of
sludge disposal and will give the most
desirahle measure of flexibility of
operation.
65-0465
Kiefer, B. The joint elimination of
sewage sludge and waste. Staedtehygiene,
16(8):179-181, Aug. 1965.
At a meeting of the work group for Baderi
Wuerttemberg of the German Water Pollution
Control Association, the purification and
incineration plant which is presently
being constructed in Ebingen was discussed.
The costs of the plant are estimated to
amount to about 12 million DM. The
purification plant will consist of a
trash rack, a sand filter, 4 settling
tanks, one accelerator (38.20 m in
diameter), and one cyclator (33.80 m in
diameter). The waste will first be
crushed in a hammer mill and the iron
parts separated by magnet. The waste
thus prepared for incineration goes to a
storage room. A conveyor belt brings
the waste to the furnace which consists of
several compartments. The sludge from the
purification plant is dehydrated to a
water content of 60 to 65 percent and
passed to the uppermost compartment of the
furnace. One hundred tons of waste are
added to 36 tons of sludge. In the upper
compartments the sludge is dried. The
waste goes directly to the incineration
compartment which is located in the
center of the furnace. The operating
costs of the plant are calculated to be
4.10 DM per cu m of sludge and 9.30
DM per ton of waste. (Text-German)
'fresh water' unit was retained as a
control. Samples were also taken to
measure the carbohydrate and protein
contents of the sludge. The degree of
cell lysis accompanying changes in salt
concentration was studied. The response
of a fresh water activated sludge to slug
does of sodium chloride of 30,000 mg per
liter and 45,000 mg per liter is shown in
graphs. The former dosage caused some
retardation in the rate of substrate
removal as compared to the fresh water
control. The solids production in the salt
unit was only 76 percent of that in
the control. The concentration of 45,000
mg per liter sodium chloride affected the
biochemical resDonse of the sludge more
severely, causing a considerable degree of
lysis and an increase in COD. Data
indicates that considerable amounts of
metabolic intermediates or end products are
released during glucose metabolism.
Changes in carbohydrate and protein
content of the sludge during the aeration
period for batch activated sludges
acclimated to various salt concentrations
are compared to those growing in fresh
water medium. The effects of placing
cells grown in Nad in lower salt
concentrations and in fresh water medium
are shown. At a cell concentration of
555 mg per liter, the maximum COD
released was 90 mg per liter for cells
grown in 45,000 mg per liter sodium
chloride. A linear relationship exists
between the change in salt concentration
and the degree of lysis. When sludge
acclimated to 45,000 mg per liter sodium
chloride was placed in fresh water the
substrate removal efficiency of the
system was almost entirely disrupted.
650466
Kincannon, D. F., and A. F. Gaudy. Some
effects of high salt concentrations on
activated sludge. In Proceedings; 20th
Industrial Waste Conference, Lafayette,
Ind., May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.316-328.
Batch activated sludge units were developed
from an initial sewage seed using a synthetic
waste. To determine the effects of slug
doses of salt, the mixed liquor from a
batch unit was divided into two equal
parts. Both n€;w units were then fed the
standard waste and one was shock-loaded with
the salt concentration under study. The
65-0467
Knapp, J. W., and J. M. Morgan.
Biodeeradability of detergents at
Manassas Air Force Station. In
Proceedings; 20th Industrial Waste
Conference, Lafayette, Ind., May 4-6,
1965. Purdue University Engineering
Extension Series No. 118. p.737-745.
A field study of the comparative
removal efficiencies of ABS and LAS
detergents was conducted during the
summer of 1964 at the Manassas Air Force
Station near Manassas, Virginia. The
treatment plant is shown in a schematic
and described. In Phase I, background
data were gathered on plant operating
conditions and detergent removals. At
the beginning of Phase II the plant
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0465-0469
was emptied and LAS products were
distributed station-wide. Phase III was
similar to Phase I but with only LAS
products in use. No significant foaming
was observed in any of the test phases.
Influent and effluent concentrations of
MBAS for the principal test phases are
represented by three-dav moving averages
shown in a graph. Increased usage did
not result in raised MBAS concentrations
entering the plant, in fact, at the
beginning of Phase III the influent
concentrations had fallen to unexpected low
levels. After 18 days of observing low
concentrations of active material, a
supplemental feed of LAS was added to
the plant. Supplemental loading was
continued and was designated Phase IIIB.
Average concentration and removals for
the principal phases are shown in a
table. Effluent concentrations of
KBAS during the LAS phases were less than
one-half of the effluent concentrations
during the ABS phase. The distribution of
MBAS and BOD sample concentrations in
the influent and in the effluent are
summarized in tables. The relative
inefficiency of ABP degradation during
Phase I is portrayed. Throughout the
LAS nhases, samples vere subjected to
infrared analysis. The 3-month study
confirmed the improved biodegradability of
LAS detergent products.
65-0468
Knopp, P. V., L. J. Uhren, M. S. Nichols,
et al. Kettle moraine field study. In
Proceedings; 2Qth Industrial Waste
Conference, Lafayette, Ind., May 4-6,
1965. Purdue University Engineering
Extension Series No. 118. p.745-754.
The removal of ABS and LAS were compared
by an 'extended aeration' activated
sludge plant under field conditions.
The efficiency of LAS removal was measured
under good and poor operating conditions.
The Kettle Moraine Boys' School and its
sewage treatment plant (shown in a
schematic) is described. The percent
removal of MBAS, suspended solids, BOD,
the DO of the mixed liquor, the return
sludge suspended solids, average daily
flow, recirculation flow, and aeration
rate are summarized. The percent removal
of MBAR and BOD are plotted. Phase II, in
which detergents containing ABR were in
use was characterized by high (anproxinatel^
8,000 mg per liter) mixed liquor
suspended-solids concentration in the
aeration tank, and high aeration and
recirculation rates. Average effluent MBAS
concentration was apprrximately 1.0 ng
per liter, the average MBAS removal was
89.9 percent while the average BOD
removal was 97.2 percent. During Phase
IV, the aeration rate and the
recirculation rate were increased to the
conditions of Phase II. The MLSS, hovever,
was 3,500 mg per liter as compared to
8,400 mg per liter during Phase II.
During the first few days of Phase TV,
a filamentous growth developed in the
sludge which cleared up prior to the
sudden drop in effluent MBAS concentration
suggesting that lower effluent MBAS
concentrations might have occurred
earlier in Phase IV if the poor settling
characteristics had not developed. At
the beginning of Phase V the aeration
rate was reduced and the recirculation
rate, was set to equal that of Phase II
and IV. The mixed liquor dissolved oxygen
decreased to zero and solids were lost in
the effluent.
65-0469
Liquid digested sludge as manure. Water
and Waste Treatment, 10(6):301, Mar.-Apr.
1965,
Sludge disposal in a manner that is
valuable to the agricultural community
has been a problem for some time. In
a paper presented by E. G. Coker to a
meeting of the Institute of Sewage
Purification at Cambridge, it was
recommended that sewage sludge be
disposed of after digestion by application
in the liquid form to grassland or
agricultural crops. Liquid digested
sludge was applied at rates sufficient to
supply the same quantities of nutrients
as contained in commercial artificial
fertilizers and the results were compared
with those obtained by artificial
fertilizers. The effect of using
supplementary potash fertilizers was
also determined. In all the tests,
the liquid digested sludge gave an increase
in dry matter similar to that produced
by equivalent amounts of nitrogenous
fertilizer. The average amount of
nitrogen taken up from liquid digested
sludge was 86,3 percent of that taken
UD from equivalent artificial fertilizers.
The liquid digested sludge gave a marked
stimulus to growth of ryegrass in
comparatively dry summer conditions
by providing water to carry the nitrogen
into the turf. Less positive results
with air dried sludge could have been
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Industrial Wastes
caused bv the loss of soluble nitrogen
during drying. Any ill effects from the
use of sludge nay be minimized by a thin
spreading of tie sludge at infrequent
intervals. These results should be
helpful in making the use of liquid
digested sludge more acceptable to
farmers.
65-0470
Lively, L., A. A. Rosen, and C. ".
Mashni. Identification of petroleum
products in water. In Proceedings; 20th
Industrial Waste Conference, Lafayette,
Ind.. May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.657-661.
Methods for hydrocarbon pollution include:
gravimetric and volumetric analyses, mass
spectrometry, and infrared spectrometry.
Sampling procedures are described: the
carbon adsorption method and liquid-Liquid
extraction proA'ed the most suitable. The
analytical methods described were
used to identify the petroleum products
found in four Incidents caused by
hydrocarbon pollution. The investigations
are given in the form of case histories.
One incident involved a private well
servLne a country store. The well water
was reported to have a gaseous taste and
a gasoline-like odor. The identity and
concentration of the pollutants
found are summprized in a table. The
comoonents detected constituted a
molecular range much narrower than IE;
typical of gasoline. This range agrees
with a number cf solvents: petroleum
ether, rubber solvent, and crude hexane.
Hydrocarbons were shown to be responsible
but the specific hydrocarbon product
VPS not identified. Other case histories
involve incidents with gasoline pollution,
kerosene pollution, and fuel oil.
650471
Loehr, R. C., and T. J. Kukar. Removal
of lipids by conventional waste treatment:
methods. International Journal of Air
and Water Pollution, 9(7/8):479-485, Aug.
1965.
Although little is known of the organic
compounds introduced into surface waters
as effluent from domestic wastes, it is
known that the lipids, because of their
insolubility in water are removed to a
lesser extent than the more soluble
organic compounds. To obtain a better
understanding of lipid degradation and
removal pattern, the lipid content from
samples of sludges and treated and
untreated sewage was extracted and
identified using column, thin laver
and gas-liquid chromatographic techniques.
The lipid classes in the purified lipid
extract in percent are shown for these
samples in a table. Although primary
treatment removes lipids that are able to
settle or float, it does not alter
the proportion of any one specific lipid
class and the same linid classes were
present in the raw and settled sewages
in the same proportion. Biological waste
treatment decreased the percent of the
methyl esters, fatty acids, triglycerides,
and sterols as the lipids were adsorbed
to the sludge particles and metabolized.
The treated and untreated sewage, activated
return sludge, digester supernatant, and
digested sludee showed no methyl esters
or fattv acids with less than 16 carbon
atoms and -10 hydrocarbons with less than
18 carbons. Although biological treatment
decreased the amount, all eight classes of
lipids were discharged in the effluent
from the Topeka treatment plant.
Seventy-five percent of the lipids in the
effluent consisted of saturated
hydrocarbons, triglycerides, fatty acids,
sterols, and compound lipids.
65-0472
Luley, H. J. Industry's idea clinic. Part
1: Industrial waste automatic sampling.
Journal of the Water Pollution Control
Federation, 37(4):508-534, Apr. 1965.
The selection of the proper methods and
equipment for automatic sampling of
industrial wastes is complicated by
the lack of standard methods and a
necessitv for the development of
specialized methods. The complexitv of
the problem is evidenced by the inclusion
of 33 pictures and sketches of various
sampling devices and their use in
practice. The Industrv Idea Clinic, held
at the annual Conference of the Water
Pollution Control Federation in 1964,
provided a dialogue among the public
agencies and the equipment manufacturers
to compare specialized developments
on industrial waste automatic sampling.
The format involved a brief discussion of
an experience or idea, followed by open
discussion and questions from the floor.
The sampling equipment discussed included
everything from a beer can on a stick to
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0470-0475
a sophisticated automatic refrigerated,
self-contained unit which provides a
composite sample by collection of a
fixed volume throughout a variable
cycle. The importance of the flowmeter
in any automatic sampling system is
emphasized and the attention of the
designer is called to such innovations
as plastic flume liners, and instream
actuation of the secondary meter. The
objectives of sampling of industrial
wastes are to assist in pollution control
and to aid in the control of both waste
treatment facilities and the manufacturing
process from which the waste is derived.
65-0473
Lutin, P. A., J. J. Chibulka, and 0. W.
Malaney. Oxidation of selected
carcinogenic compounds by activated
sludge. In Proceedings; 20th Industrial
Waste Conference, Lafayette, Ind.,
May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.131-145,
The efficiency of activated sludge
treatment in removing carcinogenic
hydrocarbons from waste water by the
oxidative mechanism was studied using
activated sludges from the municipal plant
at Nashville, Tennessee; from the
municipal plant at Franklin, Tennessee;
and from the Ashland City, Tennessee
plant. The Nashville plant handles an
average of 54.0 MGD of an agglomerate
municipal waste and is a conventional
activated sewage unit. The Franklin plant
handles 0,70 MGD of domestic sewage and
laundry waste and employs aeration. The
Ashland City plant handles 0.10 mgd of
domestic sewage with no industrial wastes
and eiroloys extended aeration (aerobic
digestion). The compounds have all be
demonstrated to be carcinogenic to
laboratory animals when ingested or
contacted ectodermally. Incubation was
at 20 C with constant motion for 144 hr.
All chemical substrates were exposed to
all sludges. Respiration of the sludge
alone was measured and used as a control.
Detailed results are given in 6 figures.
None of the carcinogens were significantly
oxidized by any of the activated sludges.
The possibility that a substrate
concentration of 500 mg per liter was
toxic to the sludge microflora in a
suspended solids concentration of 2,500
mg per liter lead to a further series of
runs with a few of the carcinogens at a
suspended solids concentration of 5,000
mg per liter. Benzyl alcohol was
included as a positive control. Doubling
the bacterial population produced no
change in the oxidative patterns of the
carcinogens. Apparently the threat of
finding carcinogens in waste waters
is not eliminated by the possibility of
sludge oxidation.
65-0474
McCoy, J. H. Sewage pollution of rivers,
estuaries and beaches. Public Health
Inspector, 74(2):79-86, Nov. 1965.
Hazards arising from the disposal of
crude sewage and sewage effluent to
natural waters are the creation of
nuisances and the transmission of infectious
diseases. The continuous discharge
of such sewage into a body of water in
excess of the water's capacity for
self-purification results in grossly
polluted water. In studies conducted over
the period of 1 year, the day-to-day
median count of Escherichia coli varied
in inverse ratio to the volume of effluent.
Salmonellae infection from consumption of
sewage polluted water tends to remain in the
community longer due to individuals who
excrete the organisms into the sewage and
ultimately into their water, causing the
reinfection of themselves and others. When
sewage is discharged into a moving
waterway, purification is greatest the
first 2 miles of the river. In estuaries,
fecal organisms survive only for a short
period of time due to the chemical content
of the water. Disposal into the open
sea results in pollution of the area
around the place of discharge, but the sewage
is quickly dispersed by winds, currents, and
tides. Seafood taken from an area which
is polluted can lead to typhoid infection.
The conclusions drawn are supported
by data from actual experimentation. Methods
which will reduce the chances of
infection are: (1) screening of sewage;
(2) maceration of the sewage; (3)
relocation of the sewage outfall pipe;
(4) removal of solids; and (5) full
treatment of sewage.
65-0475
McKinley, J. B. Wet air oxidation
process. Water Works and Wastes
Engineering, 2(9):97-99, Sept. 1965.
Wet air oxidation is a method of
burning organic matter dissolved or
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Industrial Wastes
suspended in water, without high degree
dewatering and incineration. It produces
a small volume of inert ash suspended in a
sterile, supernatant liquid without fly
ash and soot. The Wheeling, West Virginia
Sanitary Board selected this method for
sludge handling and disposal. To 1965,
the plant had processed 5.4 million ga]
of sludge 1,610 tons dry solid) at an
operating cost of $19.97 per ton of solids,
averaging 90 percent inorganic solid removal.
Total time for system start-up is 4 hr;
shutdown may be temporary, up to 24 hr, or
complete, requiring 4 hr. Routine
maintenance, indicated by temperature
and pressure drops, consists of washing
the system and occasionally changing
valve trim. The unit operates only 10
days of the expected 20 days per month,
since the oxidation plant is run above
the design rate. Other results are found
in included tables. The cost of the
installed unit was $284,000. Future
expectations of cheaper prices for
chemicals and start-up fuel plus more
frequent and longer processing runs are
forecasted to reduce costs to about
$17.00 per ton. The entire operation at
the water pollution control plant is
portrayed in two diagrams. The first one
shows the processes occurring before the
sludge is oxidized; the other shows
the processes occurring during and after
oxidation.
65-0476
McWhirter, J. R. Fundamental aspects of
surface aerator performance and design.
In Proceedings; 20th Industrial Waste
Conference, Lafayette, Ind., May 4-6,
1965. Purdue University Engineering
Extension Series No. 118. p.75-92.
Methods for determining the oxygenation
capacity of aeiation equipment include:
(1) unsteady-state aeration of pLre tap
water; (2) the steady-state oxidation
of sodium sulfite solution; (3)
steady-state aeration of activated sludge
systems, and (4) the unsteady-state
aeration of activated sludge. These are
all discussed, formulas given for the
theoretical basis of each, and a new
method (steady-state aeration of pure
tap water) presented. In testing
aerators it has been found extremely
difficult to prevent a concentration
gradient from developing in the liquid
at the start of the aeration. This can
result in the calculation of a mass
transfer coefficient which is low by
10 to 20 percent. A steady-state
reaeration technique was devised to give a
further independent check of oxygenation
capacity in pure water. This technique
gave results about 10 percent higher
than those obtained with the unsteady-state
technique and in good agreement with the
estimated error in the unsteady-state
results. Sulphite oxidation data can only
be interpreted by taking into account
the effect of the rapid sulphite-oxygen
reaction on the overall mass transfer
rate. The simultaneous gas absorption
plus reaction process can result in a
significantly higher total mass transfer
rate than the corresponding pure physical
gas absorption process. Sulphite oxidation
data in general show higher oxygen uptake
rates than corresponding steady-state
reaeration data. They also show a
different temperature variation and a
significant variation in oxygen uptake
rate with different catalysts. Determination
of quantitative design data or evaluation
of aerator performance in an operating
treatment system can best be done by
detailed analysis of the mass transfer
relationships.
65-0477
Magnus, M. N. History of fly ash
collection at the South Charleston plant
Union Carbide Corporation - Chemicals
Division. Journal of the Air Pollution
Control Association, 15(4):149-154 , Apr.
1965.
A summary is presented of the installation
and operation of fly ash collection and
disposal equipment for coal fired boilers
with a capacity of 1 ,900 tons of coal
and 328,000 Ib of fly ash a day. Tables
are given which show the capital investment,
the precipitator replacement costs per Ib
of steam generated, electrostatic
precipitator performance data, operating
costs, repair and maintenance costs, a
summary of typical installation costs, fly
ash collection summary, and fly ash
analysis. The fly ash released to the air
is 36,850 Ib per day. Ash in the coal (12%)
amounts to 456,000 Ib per day. The cost
of fly ash collection and disposal
equipment was $900,000 with a replacement
value of $1,640,000. The operating
and maintenance costs are $78,800 per year.
Fly ash from two of the boilers is removed
by means of a vacuum pneumatic and bin
storage system which contains primary and
secondary receivers, a steam ejector, spray
condenser, and a storage silo with a
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0476-0480
bag-vent filter. Fly ash from all of the
other precipitators is sluiced to low
areas around the plant for reclamation of
unusable land. One tract, worthless
because of flooding, has been filled to a
depth of 20 ft and 12 acres of the filled
land now used as a recreation area is
worth $370,000 as undeveloped land. There
is a need for greater latitude in
precipitator design as it pertains to
gas flow rates. In 6 of 8 installations,
apparent gas flows were above the
precipitator design conditions and the
efficiencies were unsatisfactory. Changes
in coal characteristics have a direct
effect on precipitator efficiencies.
Extensive cost, performance, operation and
technical data on electrostatic precipitators
is presented.
65-0478
Manufacturer cuts waste cost 42% with
stationary compactor. Refuse Removal
Journal, 8(8) :32, 58, 60, Aug. 1965.
The Owens-Corning Fiberglass Corp.'s
plant at Santa Clara, California, installed
a stationary compactor, which has cut
scrap hauling and disposal costs 42
percent. The compactor consists of a
steel plate box, one end of which is a
ram powered by a hydraulic cylinder. The
ram compacts by driving the refuse into
a trailer connected to the open end of the
compactor. The trailer, designed to
carry 18 tons, also has a hydraulic pump,
which unloads the refuse at a landfill.
industrial process, etc. can be reclaimed
from the industrial photosynthesis process.
'Industrial photosynthesis' refers to the
process of growing a complex population
of micro-organisms, predominantly
unicellular algae, under control. The
growth media are complex liquid organic
substrates, such as primary or secondary
waste water effluents. A photosynthetic
system is selected when any thin film of
aqueous organic medium is exposed to
high light intensities. The three
experimental photosynthetic reactors
tested are oval-shaped, cement-lined
structures with a sump and dam on their
left sides. The productivity of the
three reactors was measured by both the
algal cell density and the packed cell
volume. Growth rate parameters are given
for the three growth phases and the
population composition for the 3 reactors
are shown in graphs. The extensive amount
of variation observed for the reactor
growth averages was a direct result of the
extensive amount of divergence between
the average cell densities of the three
reactors; pH changes, and the temporal and
absolute relationship between the levels
of total alkalinity and pH are shown in
graphs. For the pH levels obtained there
was no apparent change in the relative
species frequency profiles. Both
bacterial and algal snecies in the three
reactors were identical. The data showed that
the conditions of the reactors select
against both total bacterial population
and specifically against the coliform
component.
650479
Mattoni, R. H., H. N. Myrick, and E. C.
Keller. Application of industrial
photosynthesis process to waste water
renovation systems. In Proceedings; 20th
Industrial Waste Conference, Lafayette,
Ind., May 4-6, 1965. Purdue University
Engineering Extension Series 118.
p.684-705.
In 1964, North American Aviation, Inc.
constructed and has since operated
three experimental pilot-scale photosynthetic
reactors in Lancaster, California, to define
the potential uses of the industrial
photosynthesis process. The applicability
of the process to waste water renovations
systems was studied. Water, suitable
for use in irrigation industrial
processes, etc. and biomass, which may
be used for animal feed, carbon input for
65-0480
Matusky, F. E., J. P. Lawler, T. P.
Quirk, et al. Preliminary process design
and treatability studies of fish
processing wastes. In Proceedings;
20th Industrial Waste Conference, Lafayette,
Ind., May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.60-74.
A plant has been designed for the treatment
of wastes from fish and chip processing
and domestic sewage. The major problem
was to determine the effect of the fish
wastes on the combined treatment system. A
study of an existing fish plant was made
as well as a laboratory digestion study
of combined fish, potato, and municipal
waste. Production methods were observed
at the plant and compared to the proposed
fish processing layout. Waste samples
were collected at various points in the
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Industrial Wastes
present plant and BOD, COD, suspended
solids, oxygen transfer coefficient, and
pH determinations made. The pH ranged from
6.5 to 7.5 and no difficulties in
treatment was anticipated because of
pH. Grease content varies with the kind
of fish processed; cod and haddock have
a grease content about 0.3 percent by
weight while fat fish like halibut or
herring have a grease content about 6
percent by weight. A high grease content
inhibits oxygen transfer in an aerated
biological waste stabilization system.
Treatment-plant design loadings were
computed for 1969 fish production
estimates of 40,000 ton per year raw
fish, 3,000 Ib per hr potato sticks and
a town population of 4,000. Complete
treatment of the anticipated waste
includes removal of coarse solids, oil
removal, conversion of dissolved solids
into sludge, sludge separation and
disposal, and final effluent sterilization
and disposal. A flow diagram for the
proposed plant is given. The digester
experiments indicated that a mixed
waste of fish, potatoes and sewage
sludge can be digested at loadings of 0.1
to 0.36 Ib VS/CF. At higher loadings
digestion efficiency decreases as
indicated by a marked drop in gas
production per unit of volatile material
destroyed and souring of the digester
becomes possible. The digestabllity of
lean fish, fat fish, and fish oil were
almost identical and no difficulties are
expected from production schedules that
segregate the type of fish. Other
experiments were carried out and results
are reported.
65-0481
Mercer, W. A., W. W. Rose, and E. S.
Doyle, Physical and chemical
characterization of the fresh water
intake, separate in-plant waste streams
and composite waste flows originating
in a cannery processing peaches and
tomatoes. Cannery Wastes Research Keport
No. 1. Washington, National Canners
Association, Mar. 1965. 213 p.
Data acquired in determining the physical
and chemical characteristics of the fresh
water intake, separate in-plant waste
streams and composite waste flows originating
in a cannery processing peaches and
tomatoes is given in 77 tables, 50 figures.
A diagram of the plant, showing locations
of the meters, is included along with a
description of the meter itself and
pertinent factors affecting results. The
physical and chemical characteristics of
water samples taken over a period of time
for separate and combined peach and tomato
operations are given and the analytical
procedures followed described. The
purpose of these investigations was to
characterize strong and weak waste to
make possible separate treatment or
disposal of a smaller volume of liquid
containing most of the organic waste
load otherwise diluted in the total waste
flow. The sampling procedures followed
are outlined and photographs of various
plant operations are included.
650482
Middlebrooks, E. J., A. J. Panagiotou,
and H. K. Williford. Sludge accumulation
in municipal sewage lagoons. Water and
Sewage Works, 112(2):63-68, Feb. 1965.
Field data were collected from sludge
samples at 15 lagoons of varying age and
size in Mississippi, which treat municipal
raw sewage and industrial wastes, to
develop a rough guide for evaluation of
rate of sludge accumulation. A minimum of
18 samples were collected in each Lagoon
with consideration given to direction
of prevailing winds. Sludge and soil
depths were recorded and the sludge
portions of the samples were composited
for analysis. The details of construction
of the clear plastic sampling tube used
are shown by diagram. Pertinent data about
surface area acres, age at sampling date,
BOD, loading, percent total solids and
percent volatile solids of composited
sample, and average sludge depth in
inches of selected lagoons are tabulated.
Depth of sludge in inches for the
sampling lines parallel and perpendicular
to the prevailing winds is listed by
table for each lagoon, showing that:
where a sampling line culminates in a
corner of a lagoon, there is a greater
accumulation of sludge in the corners.
Depth of sludge near inlet points along the
sampling lines parallel and perpendicular
to the prevailing winds are given by table,
showing sludge concentrations at all inlet
points. The rate of sludge accumulation as
observed in the investigated lagoons is
described in terms of a regression
equation based on the parameters of age
of lagoon, applied BOD loading rates, and
average percent of total and volatile
solids. The largest source of variation.
70 percent is explained by the age
factor. The interaction between total
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0481-0485
and volatile solids is the second largest
source of variation in terms of effect
on sludge depth. Extrapolation of the
equation indicates that the rate of sludge
accumulation is 1 ft per 27.6 years.
65-0483
Net-/ sawmill chooses Bijoli baler. Waste
Trade World, 106(3):12, Jan. 16, 1965.
The problem of disposing of 50 to 60
tons of chippings and sawdust from a new
sawmill at King's Lynn in the most
economical manner was solved by the use
of a Bijoli baling press. The wood waste
is controlled, conveyed, and collected
by three installations. In the box
wood mill, the waste from a 7-in. molder,
a surfacer, a tenoner, and various cross-cut
saws are exhausted through a 10-ft
diameter cyclone by a 16,500 cfm
capacity fan. The planing and saw mill
with two 12-in. planers, 4 molding
machines, two 54-in. band resaws, and a
36-in. circular saw are exhausted through
a 14-ft cyclone by two fans with a
capacity of 36,500 cfm. Discharge pipes
from the roof cyclones provide a constant
feed to the baler with a provision for
diversion of excess to adjacent bins
during peak production. The waste in the
storage bins can be conveyed pneumatically
back to the baler when required. The
installation operates as an integrated
unit in the production plan ard handles
the waste from the point of generation
until the baled waste is ready for
shipment to outside contractors who purchase
the material. Prior to the installation
of the baler, the transportation of the
waste in bulk form was expensive and
untidy. The two fans used on the
planing and sawing mill are employed to
give an optimum economy. The fan
discharges are fitted with counterbalanced
dampers to prevent dust from entering the
plant.
65-0484
Niemitz, W. The heating value of sludges
and its relationship to other sludge data.
Wasser und Abwasser, 106 (50) : 1 392-1 395 ,
Dec. 1965.
Two types of heating values must be
distinguished, upper and lower, depending
on the evaporation heat of the water feed
in combustion. The upper heating value,
BOD, and carbon and hydrogen contents of
the solids of a number of sludges were
determined and listed in a table, indicating
the close relationship between the
heating value of activated sludges and
their loss on ashing. The values of
fresh sludges with 1 g of loss on ashing
are higher by about 10 percent due to
the fact that they are composed of a
greater amount of hydrogen-containing
compounds. The lower heating values
establish a better relationship to the
loss on ashing in this case. No difference
at all exists between the loss on ashing
obtained between 500 and 800 C and the
heating value (data are listed in a
table). British scientists first tried
to express this relationship in a
mathematical formula. In Germany the
Fair-Geyer equation is the best known.
It assumes that the sludge is dehydrated
with the aid of chemicals prior to
incineration and takes account of the
origin of the sludge, making the calculation
rather complicated and inaccurate. An
equation was established to derive the
upper heating value from the loss on
ashing: Y (upper heating value) = X
(loss on ashing/500 C/in percent of
solids) x 83.3 - 1089. (Text-German)
65-0485
Niemitz, W., and K. Fuss. The specific
filter resistance and the compressibility
of sewer sludges, Wasser und Abwasser,
106(28):778-783, July 1965.
Specific filter resistance is based on
the filtering velocity of a sludge under
defined conditions. An equation for
calculating specific filter resistance
r of a sludge is given, the equipment for
its experimental determination is
illustrated, and r is determined for
31 different sludges, divided into
four groups. The mean values for r
calculated from the experimental data, are
given along with maximum and minimum
values. No major difference exists in the
dehydration ability between fresh and
activated slud ;s. Chemical substances in
the sludges cause neither a noticeable
deterioration nor a clear improvement of
r; however, considerable influences into
both directic are possible. Extensive
thickening of the sludge makes a more
economic dehydration possible, but no
definite correlation was found between these
two values or between r and the thickening
ability. Sludges with a low loss on ashing
generally also have a low r. The lower r is,
the more attention must be paid to maintaining
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Industrial Wastes
sludge structure. Since r is a function
of pressure, the compressibility of
sludge can be derived. The degree of
improvement of r by adding flocculants is
important for the dehydration behavior
of sludges. (Text-German)
65-0486
1964 Meeting of the Association for Water
Pollution Control. Wasser und Abwasser,
106(18) :501-503, May 1965.
The Association for Water Pollution
Control held its 1964 meeting on
September 23 and 25, at Ebingen, Germany.
Among the many papers presented, which
dealt mainly with water pollution problems,
one treated the common elimination of
sewage sludge and waste. Two methods
allow for a combined treatment of waste
and sludge, namely, incineration and
composting. The greatest reduction of
volume is achieved through incineration.
The annual amount of sludge is reduced
from 550 liters per year to 10 liters per
year, of waste from 700 liters per year to
60 liters per year. For comparison,
about 200 liters per year remain from
composting. Prior to composting, the sludge
must be dehydrated to a water content
of 50 percent. The water content also
plays a role in the incineration. If
the waste has a water content of 35
percent, an incineration without
additives is still possible even when
the fresh sludge has a solids content of
only 11.5 percent and the activated
sludge 13.5 percent. The incineration of
sludge and waste can be carried out either
in the conventional incinerator or in a
rotating furnace. In any case the sludge
must be dehydrated to some extent prior
to incineration to achieve satisfactory
results. (Text-German)
65-0487
Nusbaum, I., and L. Burtman. The
determination of floatable matter in
waste discharges. Journal of the Water
Pollution Control Federation, 37(4):577-583,
Apr. 1965.
An apparatus was developed which can be
used to provide a standard test and
establish criteria for floatable matter in
wastes, especially those discharged
through ocean outfalls. A sketch is
given of the polyethylene drum, 13 in.
in diameter and 24 in. high, which would
contain 12 gal of sample. Small
plastic couplings used to remove the
upper layer of the sample were 3% in.
in diameter and 3 7/8 in. high. In
tests, the drum was filled to the 21 in.
mark and the coupling was lowered into
the device until the rim just touched the
water surface. After 60 minutes a smooth
plastic ball slightly larger than the
coupling was slid under the surface to
seal the coupling. The glass-fiber filter
paper method was used to determine the
filtrable solids before and after settling
and a wet extraction method was used to
determine the grease and oil. Two tables
are given showing the floatable matter
as filtrable solids and grease before and
after settling at the San Diego Sewage
Plant and at other plants in the vicinity.
The information already obtained shows a
considerable accumulation in primary and
secondary effluents of filtrable solids
and solvent extractable materials in the
surface layers. San Diego primary effluen"
shows a geometric mean of 89 mg per liter
before settling and 145 mg per liter at the
surface after settling for one hour.
Additional testing is indicated before
the apparatus is fully accepted.
65-0488
Orderly and controlled deposition of
industrial waste. Staedtehygiene,
16(12) :272-275, Dec. 1965.
A group of German institutes concerned
with the question of solid and liquid
waste disposal jointly issued a pamphlet o.i
the controlled dumping of solid waste
in landfills. It is of utmost importance
to prevent water soluble harmful
substances from reaching the: groundwater.
This is done by selecting a proper
landfill site, by sealing the ground with
a layer of clay, packed soil or plastic
material, and to some extent by sorting
the waste according to harmfulness and
water retention. Glasses, ceramics,
soil and building debris pose no problems.
Other waste is usually deposited in layers
which are 1.5 m thick. To red'jce water
seepage, packing to increase' the density,
is advisable. Thin intermediate layers
of soil, gravel, slag or debris prevent
the wind from carrying away light material
and provide a surface for motor vehicles.
Inorganic water soluble waste is covered
by layers of organic material with high
water retention capacity. Dumping sites
must be well-planned and managed. Flooded
gravel pits must not be used as landfill
sites since they are connected to the
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0386-0491
groundwater system. Swamps, although they
seeir to be isolated from the groundwater,
may subside, thereby reaching the water
table. Abandoned quarries and ground
depressions must be checked for leaks.
Landfills, when properly covered by a
layer of soil 0.3m thick, can be
cultivated. They may also be used as
recreational areas. For reforestation,
only trees with a shallow root system are
suitable because deep roots might penetrate
the water-damming layers and cause seepage
into the ground water. (Text-German)
65-0489
Paper and paper wastes - an operations
analysis. Public Works, 96(10):146,
148, Oct. 1965.
An article, 'Studies in Force Main
Aeration', by James E. Laughlin in Journal
of the Sanitary Engineering Division,
Proceedings of the American Society of
Civil Engineers, December 1964, is
reviewed. By 1963, the waste treatment
facilities of the Covington Mill of the
West Virginia Pulp and Paper Co. were
handling over 50,000 Ib per day of BOD--
an increase of about 30,000 Ib per day
over the 1955 load. Although the treatment
plant has not been enlarged, high
efficiency has been maintained. The
primary clarifier suspended solids removal,
with inclusion of additional mill flows
and the addition of a primary clarifier,
is about the same. An improvement is
noted in primary BOD removal efficiency.
The effect of aeration detention time
and mixed liquor solids on BOD removal
during bio-oxidation treatment
can be expressed by a suitable relationship.
The rate co-efficient is influenced by
variations in waste characteristics,
temperature, and nutrient level. At
temperatures greater than 100 F, the
BOD removal efficiency is impaired. The
effect of nitrogen deficiency on BOD
removal is greatest at the highest
temperatures. Increasing the nitrogen
feed above 4.5 Ib N per 100 Ib BOD
removed, exerts only a slight
influence on BOD removal.
65-0490
Pfeffer, J. T., A. A. Samra, and D. T.
Schwegler. Trace metals and filamentous
micro-organism growth. In Proceedings;
20th Industrial Waste Conference, Lafayette,
Ind., May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.608-617.
A sample of raw sewage from the Lawrence,
Kansas, sewage treatment works was aerated
by shaking with a New Brunswick scientific
Model G10 Gyrotory Shaker at 200
cycles per minute. A synthetic substrate
(details of its constituents are given in
a figure) was fed to the flasks daily.
About 30 minutes were allowed for solids
separation after which 2/3 of the flask
volume was wasted. This was replaced by
the substrate. To encourage growth of
fungi over bacteria individual trace
metals were eliminated from separate
flasks. The growth of the fungi on a
specific substrate was measured. Six trace
metals were investigated: iron, manganese,
zinc, cobalt, copper, and molybdenum. Of
the fungi studied, only iron and zinc
were of significance to the organism's
growth. Copper inhibited the growth of
all cultures on the media employed.
The trace metal requirements for filamentous
fungi are different from those of bacteria.
When the trace metal required for bacterial
growth is missing, fungi will predominate
and sludge bulking will occur. Good fungal
growth was obtained in glucose with only
iron or zinc present. These were the
only trace metals of significance to
fungi, except for copper which retards
growth particularly on lucose. (The
effect of copper on the acetate media
was not as great as for glucose.) The
chemical environment is important in
controlling the availability of trace
metals; ferric iron is extremely insoluble
in natural waters and waters high in
phosphates. Ferrous iron is more
soluble. Zinc is reasonably soluble
in natural waters, but not in the
presence of high concentrations of phosphate.
65-0491
Pfeiffer, B. V. H. R. Zablatsky, J. B.
Hazen, et al. Industry's idea clinic.
Part II: Disposal of industrial waste
treatment plant sludge. Journal of the
Water Pollution Control Federation,
37(4) :535-563, Apr. 1965.
The treatment methods developed for
industrial wastes in one industry may
not be applied in another or the advantages
of treating industrial wastes and their
accompanying solids with domestic
sewage may not be recognized. The
Industry Idea Clinic at the Annual
Conference of the Water Pollution Control
Federation in 1964 gave the representatives
of industry and public agencies an opportunity
to exchange information of mutual benefit
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Industrial Wastes
on technical problems. The format involved
a brief discussion of an experience or
idea, followed by open discussion and
questions from the floor. One table shows
typical data of BOD and suspended solids by
industry. The average BOD from Daper
pulping was 2,789 mg per liter and BOD
from an industrial community was 360,
compared to a residential community with
129. The highest average and the highest
values for suspended solids were from
waste stock and coating in the paper
industry with values of 1,791 mg per liter
for the average and 6,320 for the highest
result. There are two sketches of the
effluents from a copper smelter; sketches
showing the use of digested and activated
sludge for chemical waste degradation; and
a diagram of a two-stage long-term Lagoon.
Tables and charts given include: effects
of centrifuging sludge; the properties of
digested and activated sludge; and
reduction of solvents and degradation of
toxic organic chemicals by digested sludge.
The report to the Idea Clinic includes a
state-of-the-art.
65-0492
Pipes, W. 0. Carnivorous plants in
activated sludge. In Proceedings; 20th
Industrial Waste Conference, Lafayette,
Ind., May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.647-656.
Samples of activated sludge from the
experimental pilot plant at the Sanitary
Engineering Research Laboratory, University
of California, Berkeley (capacity of
aeration tank: 600 gal and aeration
time: 6 hr) were examined for predatory
fungi. The carnivorous fungi found in
activated sludge prey either on nematodes
or rotifers: thus, the way to find these
fungi is to look for dead nematodes and
rotifers, and, when one is found, to
examine it closely to see if it is
attached to a fungal hypha or if there
are hypae inside it. The hvphae of
predatory fungi are more slender than
those of some other fungi, but they are
large enough to be easily distinguished
from filamentous bacteria. A dead
nematode may contain predatory fungus not
readily apparent and therefore a sludge
containing large numbers of dead nematodes
should be examined by the enrichment
technique. Two enrichment techniques
were used: one consisted of placing
a fairly large sample of activated sludge
on a medium which would encourage the
growth of rotifers and nematodes; the other
consisted of placing a small sample of
sludge in a dense culture of either
rotifers or nematodes. The fungi
recovered are described in detail and
illustrated in figures. One fungus was
somewhat similar to Zoophagus insidians
Sommerstorff but is designated as
Zoophagus sp. Results of the sludge
volume index determinations on the
fill-and-draw cultures of Arthrobotrys
are given in a table. When the fungus
was grown saprophvtically on sewage with
bacteria and protozoa, it formed a
compact, readily settleable sludge. When
large numbers of nematodes were added, the
mycelium development of the fungus
became more extensive and the sludge
volume index increased. The media
for enrichment cultures of predatory
fungi are given in an appendix.
65-0493
Poloncsik, S., R. B. Grieves, and W. 0.
Pipes . Process optima in activated
sludge. In Proceedings; 20th Industrial
Waste Conference, Lafayette, Ind., May
4-6, 1965. Purdue University Engineering
Extension Series No. 118. p.197-209.
The effects upon the activated sludge
process of: (1) baffling the aeration
tank to orovide three completely mixed
compartments of varying fractional
volumes; (2) varying the input distribution
of the waste to the three compartments;
and (3) varving the recvcle flow to the
three comnartments were studied. Two-nhase
and one-phase kinetics were used. (The
latter for the no sludge recycle.) Figures
are given of a schematic diagram of an
activated sludge model, of the effect
of volume distribution using two-phase
kinetics, and the effect of input
distribution using two-phase kinetics. The
performance equations for these examples
are developed. The results are limited by:
(1) the volume apportionment of the
aeration tank is only an approximation
of the existing hydraulic regime (but it
is a better estimate than the completely-mixed
or the plug-flow model); and (2)
concentrations of limiting nutrient and
of active sludge mass do not necessarily
correspond to the outlet BOD or suspended
solids concentrations. In most instances
the outlet five-day BOD and suspended
solids can be obtained by simple
conversion factors for the particular
system. Optimum operation is achieved
by dividing the aeration tank volume
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0492-0496
into three equal compartments. No baffling
produces the poorest efficiency. The
feed should be distributed toward the
front of the system and avoid the third
compartment if possible. If distribution
is varied between the first two
compartments only slight differences are
produced. Step aeration should be
avoided unless oxygen supply becomes the
rate limiting factor. For an equal volume
and feed distribution, the recycle
should be inserted toward the back
end of the system.
65-0494
Poston, H. W. A close look at a recent
federal enforcement conference. In
Proceedings; 20th Industrial Waste
Conference, Lafayette, Ind., May 4-6,
1965. Purdue University Engineering
Extension Series No. 118. p. 1-5.
The conference was called by the Secretary
of the Department of Health, Education,
and Welfare and involved the Calumet
River System and the southern end of
Lake Michigan. The conference was
complex in that it involved the second
largest city in the United States, the
largest water treatment plant in the
world, the drinking water and recreational
facilities for 4.5 million people. There
were 15 points of agreement
which will form the basis for abatement
and enforcement. The recommended quality
criteria goals for lake water at Chicago
intakes are given in terms of acceptable
limits on an annual average basis and
permissible limits during not more than 12
days per year. The parameters include:
coliform per 100 ml, annual limits less than
200 but 2,500 acceptable during not more
than 12 days a year; dissolved oxygen,
ppm, not less than 8 and not less than 5,
respectively; BOD, ppm, less than 1.5 and
maximum 3, respectively; and pH, average
8.2 and maximum 9, respectively. The
responsibilities of the various governmental
units to implement the recommendations
are described.
65-0495
Proceedings; Conference on Waste Disposal
for Food Processing Plants, Easton, Md .
Jan. 12, 1965. University of Maryland
and U.S. Department of Agriculture, Mar.
This conference on waste disposal for
food processing plants was sponsored by
the Cooperative Extension Service, the
University of Maryland, the Mid-Atlantic
Food Processors' Association, and the
Maryland Department of Water Resources.
The meeting exemplified the importance
of waste disposal to the food industry.
Members of the Cooperative Extension
Service along with the Regulatory
Agencies and Industry discussed the many
aspects of the problem of waste disposal
and means by which the problem could be
solved for the betterment of all concerned.
The methods available for the disposal
of solid waste and liquid waste were
discussed. To produce the industry's
annual, nationwide pack of 750 million
cases of canned foods required about 36
billion gal of water. The method commonly
used for treating domestic sewage, to
secure a high degree of purification,
involves biological oxidation by one
of several different procedures. Whether
enough water is being used or not, there
is alwavs room for water conservation
in most plants, due to actual waste
and inefficient use. Although there
are no completely satisfactory and cost-free
ways to deal with the canning waste solids
problem, the present methods are considered.
For waste disposal with sprinkler irrigation
systems the first information of concern
is the amount of waste effluent for which
an acceptable system is necessary. The
final design should be prepared by a
reliable irrigation equipment dealer who
would recommend the best adapted models
of equipment and control systems.
650496
Purcell, L. T. Raw sludge disposal by
vacuum filtration. Water Works and Wastes
Engineering, ?(9):64-65, Sept. 1965.
The raw sewage-sludge dewatering facility,
in Butler-B]oomingdale, New Jersey, has
resulted in: (1) economical operation;
(2) elimination of severe odors; and (3)
improvement of the community's attitude
toward the plant. The plant handles raw
primary settling tank and secondary solids
from 15,000 persons, and operates a
Komline-Sanderson coilfilter 3 days a
week with average loadings of 7 Ib per sq
ft per hr. It also pumps raw primary
sludge to conditioning and dewatering
equipment, and produces and disposes
of sludge cake. Numerous facilities had
been added to the existing plant with
proposed improvements based on a projected
population of 15,000 with an average
flow of 1.5 mgd. Existing digesters had
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Industrial Wastes
been the greatest problem. Vacuum
filtration was thus added to eliminate
sludge digestion and sludge drying on
sand beds. A coilfliter was installed
and existing digestors were converted
to sludge holding tanks. All sludge is
drawn from primary settling tanks and
discharged either to the holding
tank or directly to the process;
chemical conditioning of raw sludge takes
place; dried filter cake is transported
and disposed of in the abandoned sand
drying bed area. During a normal 6 hr
filter run, periodical sludpe nH and cake
production checks are made. Shut down
and cleaning of filter requires
7 hr; general maintenance occurs one day
each month when acid baths may be given.
Filter cake is sent four times a day to
disposal areas which are covered at the
end of the week.
65-0497
Purdue University. School of Civil
Engineering. Proceedings; 20th Industrial
Waste Conference, Lafayette, Ind., May
4-6, 1965. Purdue University Engineering
Extension Series No. 118. 803 p.
The 20th Industrial Waste Conference was
sponsored by Purdue University in
conjunction with the Indiana State Board of
Health. Sixty-six papers were presented.
The subjects included: federal
enforcement, fungi in sludge digestors,
low pressure wet air oxidation of sewage
sludge, fish processing wastes, surface
aerator performance, a field countercurrent
extractor for water pollutants, carbon as a
parameter in bacterial systems growth, ion
flotatior, trickling filter, agricultural
ammonia for digesters, photosynthesis,
activated sludge, biodegradability,
coliform, aerobic bacteria, pesticides,
pollution control for mining, benthos
and plankton, sludge bulking, the effects
of high salt concentrations and of
nitrogen and phosphorus on sludge,
lagooning, radioactive waste disposal,
liquid-solids separation, oxygen transfer,
dewatering, culture studies of bacteria,
trace metals, duck wastes, acid mine
drainage, sewage chlorination, spray
irrigation, algae, polyelectrolyte
coagulants, and LAS and ABS treatability.
65-0498
Quon, J. E., and G. B. Ward. Convective
drying of sewage sludge. International
Journal of Air and Water Pollution,
9(5):311-322, May 1965.
Because of the success of sludge drying
beds with only limited drainage, it is
desirable to know more about the mechanisms
of sludge dewatering. In this work, a
study was made of the rate of sludge
drying by convection as a function of the
temperature, humidity, and velocity of the
air over the sludge surface. A schematic
drawing is given of the experimental
arrangement for the determination of
sludge drying rates effected by convection.
Tables are given which show: sludge
characteristics; reduction in sludge
moisture with time; a summary of sludge
drying rates and the operating variables
of temperature, relative humidity, and air
flow; and the heat and mass transfer
coefficients. Graphs are given which show
the weight remaining versus time, the
drying rate versus the moisture content, the
drying rate versus the temperature
difference, and the drying rate versus the
humidity difference. For an air flow of 9
ft per second, a temperature of 83 F and a
relative humidity of 52 percemt, the
sludf»e drying rate was 0.092 Ib per hr-sq
ft compared to an evaporation rate from
a free water evaporation rate of 0.21
Ib t>er hr-sq ft for humidity differences
greater than 0.03 Ib moisture Pjer Ib of dry
air. The values were not particularly
sensitive to sludge depth nor to variations
in the temperature, humidity, or air flow
over the ranges studied. The high value
of ration of heat transfer coefficient
to the mass transfer coefficient suggests
that the plane of vaporization is below
the physical sludge surface.
65-0499
Quon, J. E., and T. A. Tamblyn. Intensity
of radiation rate of sludge drying.
Journal of the Sanitary Engineering
Division, American Society of Civil
Engineers, 91(SA2):17-31, Apr. 1965.
Field experience has indicated that
drying time required by the conventionally
designed and operated sludge drying beds
is comparable to that required by beds
modified to provide only limited drainage
and cleaned with mechanical equipment.
Quantitative information on the dewatering
characteristics of digested sludge is
provided and is useful for the design
of drying beds with limited drainage. The
rate of water evaporated from a sludge
surface and a free-water surface, as
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0497-0502
a function of the radiant intensity
incident on the sludge surface, was found
to be essentially equal when evaporation
was the sole mechanism of dewatering. For
an intensity of 1.00 calorie per sq cm per
minute, the evaporation rate was 0.9X per
.001 per g per sq cm per minute. The
evaporation rate from the sludge surface
was depressed by 22 percent when both
evaporation and drainage contributed to the
dewatering. One-half of the energy
incident on the sludge surface was found
to be associated with the latent heat of
vaporization. The emissivity was found
to be dependent on the wave-length of
adiation. The critica] moisture for the
sludge used ranged from 66 percent to 84
percent.
65-0500
Rabb, A. Sludge disposal: a growing
problem. Hydrocarbon Processing,
44(4) :149-150, Apr. 1965,
An investigation in the Netherlands
showed that amount of sludge depends on
the quantity of waste water treated,
degree of contamination and required
effluent quality. To minimize treating
unit costs, contaminated water storage is
provided. For a 40,000 to 50,000 bpsd
refinery, treatment rates range from 200
to 900 U.S. gpm. A table shows ranges of
impurities. Solids settling in the oil
separator, chemicals, and microorganisms
must be removed. Preparation of the
sludge for burning is basically water
content reduction. Highest practical
concentration is reached by filters.
Rotary kilns can operate with five to 70
percent solids; with 40 to 70 percent, a
stationary incinerator can be used.
Electric power cost $0.0125 per kwh; fuel
oil, $15 per ton; labor, $8,000 per man-year
based on five years of operation. Graphs
show costs and concentrations. Optimum
concentration of sludge before burning is
shown as a function of the lean sludge
quantity. Small equipment has a relatively
high cost.
65-0501
Renn, C. E. Woodbridge, Virginia, field
tests of biodegradable LAS detergents in
extended aeration activated sludge systems.
In Proceedings; 20th Industrial Waste
Conference, Lafayette, Ind., May 4-6,
1965. Purdue University Engineering
Extension Series No. 118. p.734-737.
Field tests were conducted to emphasize
conclusions previously reached about the
behavior of degradahle detergents that
may be useful in the operation, treatment,
and design of new plants when LAS base
materials come into general use. Influent
ABR concentrations were found to vary
widely (7.5 ppm to 32 pom); effluents
ranged from 2.5 ppm to 13.0 ppm. All
residents shifted to degradable LAS
materials at the same time and a rapid
decline in foam on the surface of the
aerator was noted. Effluent samples
showed declining foam levels and the
concentrations of methylene blue active
equivalent (to determine residual anionic
detergents) declined from 8 ppm to 3
ppm. High excess oxygen in the effluent
could no longer be maintained and the
aeration interval times in the cavitator
had to be increased. The BOD removal
efficiency declined steadily. Difficulties
in maintaining dissolved oxygen arose from
the change in the character of the air-water
emulsion generated with LAS-bearing waste
feed. When the old ABS sludge was pumped
out and the system started fresh, there
was a rise in BOD removal efficiencies and
a declining ABS-free effluent. The
efficiency of detergent removal was found
to be modified by overall BOD removal
efficiency, but a system operating in
the range of 80 to 90 percent BOD
removal could be expected to degrade 80
to 90 percent of the LAS. Neither
BOD removal nor LAS removal was affected
adversely by low temperatures. Loads
of LAS detergent were added to the waste
stream; average influent levels were
first brought to 25 ppm, then to 50 ppm,
and finally to 75 ppm LAS. The first
two increments were successfully
assimilated, but when essentially 225
ppm was added, the solids became too
thick to obtain effective settling.
65-0502
Rickard, M. D., and W. H. Riley. Carbon
as a parameter in bacterial systems growth
limitation and substrate utilization
studies. In Proceedings; 20th Industrial
Waste Conference, Lafayette, Ind.,
May 4-6, 1965. Purdue University Engineering
Extension Series No. 118. p.98-109.
The utility of carbon analysis in
following the metabolism of organic
compounds during the growth of a bacterial
culture in a defined medium is surveyed.
The relationships obtained among cellular
carbon, exogenous soluble carbon, and
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Industrial Wastes
viable count during bacterial growth are
shown along with the rates of synthesis of
cellular material. The method is based on
the ranid combustion of a micro sample in
oxygen and measurement of the carbon dioxide
produced with a nondispersive infrared
analyzer, Aerobacter aerogenes ATCC No.
8308 was used. Graphs show: the
calibration curve for carbonaceous analyzer,
the linearity of carbon determination on A.
aerogenes, the growth rate of A. aerogenes
in glucose, the variation in the carbon
content of viable cells, and the carbon
balance on the respiration of A. aerogenes
on glucose. Although the viable count
data show the existence of a lag in cell
division during the first two hr of
incubation, the cell carbon analysis showed
no lag in the synthesis of cellular
material. The carbon content of the cells
varied significantly as a function of the
culture age. The well-established lag in
cell division without a corresponding lag
in development of cell mass that occurs
when organisms from a stationary phase
culture are inoculated in fresh medium
means that organisms in the stationary
phase have lost the biochemical systems
necessary for cell division and that a
definite time lag phase is required for the
reestablishment of these systems. Oxygen
was an important factor in the development
of maximum populations in the non-substrate-
limited systems.
650503
Riley, W. H., and M. D. Rickard. The
biochemical aspects of aerobic bacterial
growth. In Proceedings; 20th Industrial
Waste Conference, Lafayette, Ind., May
4-6, 1965. Purdue University Engineering
Extension Series No. 118. p.235-247.
A physiological and biochemical
description of Aerobacter aerogenes
growing in liquid culture is reported. The
inoculation of these cells from a
stationary phase culture irto fresh medium
starts a chain of biochemical events that
result in a differentiation from a resting
cell to a dividing cell that has increased
its mass, DNA, KNA, and protein content.
This differentiation process is respondible
for the delay in cell division seen after
inoculation. The delay has not been
completely explained. Sub-cultures into
fresh medium from an experimental culture
show that lag phase is dependent primarily
on the ape of the culture. Dilution
during the lag phase does not lengthen
the lag period. Cell division begins
at the same time as in the parent culture.
Dilution of samples from the lag phase is
not followed by the onset of a lag period.
Sub-cultures taken during a period of
arithmetic growth do, however, have
a lag period. The environment is changed
by increases in mass and in population so
that it can longer support a logarithmic
increase in cellular material. At this
time, by some as-yet-unknown mechanism,
the cell stops logarithmic growth and
enters a period of selective synthesis.
RNA synthesis stops completely and protein
synthesis stops temporarily. The period
of arithmetic growth that follows represents
the continued increase in cellular
material necessary to return to the
biochemical composition of the resting
phase cell. The sanitary engineer would
like to find a method of prolonging the
period of logarithmic growth. It is
possible that an inoculum of logarithmically
growing cells might be useful in activated
sludge systems.
65-0504
Robert A. Taft Sanitary Engineering Center.
Interaction of heavy metals and biological
sewage treatment processes. Cincinnati,
U.S. Department of Health, Education, and
Welfare, May 1965. 201 p.
This volume, a collection of 10 research
papers originating at the Robert A. Taft
Sanitary Engineering Center, describes
the effects of chromium., copper, nickel,
and zinc on sewage treatment processes.
Results of pilot plant studies and
full-scale municipal plants are given. For
each of the metals and combinations of
metals studied, the effects on the aerobic
and anaerobic treatment processes, under
continuous dosage, are given. The data
presented allow a reasonable estimate to be
made of the amount of metallic wastes
that a treatment plant can receive and
accomplish the desired efficiency of
treatment. The effects of slug discharges
of the metals on the aerobic and anaerobic
processes under pilot plant conditions and
at municipal plants are presented. The
concentrations of the metals in the
various sludges and effluents produced
by a treatment plant are given. Metal
balances conducted for each of the studies
show the amount of metal removed by
primary and secondary treatment. The
report includes explanatory figures and
tables.
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0503-0507
650505
Rock, R. M., and N. C. Burbank.
Modifications to the Briggs micro-
electrophoretic cell and comparisons
with the Zeta-Meter cell. In Proceedings;
20th Industrial Waste Conference, Lafayette,
Ind., May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.589-607.
Micro-electrophoresis may be used to
evaluate the treatment of industrial
waters and wastes, but detailed
information on equipnent has been lacking.
Four tvnes are in use. However, the
purpose of present study was to study the
orip.inal Bripgs design, imnrove it in any
way to increase the speed of determinations
and the versatility of applications and to
compare it to the patented, manufactured
cell known as the Zeta-Meter. The original
design of Briggs is shown in a figure and
the alterations introduced shown in four
figures. Certain disadvantages of these
modifications are pointed out. The
Zeta-Meter cell is described and illustrated.
The two units were compared in terms of:
size and handling, availability and cost,
optics, stationary levels and counting
planes, timing charts, and accuracy. The
two units were found to be comparable
with respect to size, speed of
determinations, size of the smallest
colloid visible, and the values of
determinations reported on identical
colloid systems. The Zeta-Meter was found
to be more rugged, compact, and portable.
The Briegs cell was less costly, better
adapted to the determination of dense
colloid populations and to possess a wider
ran?e of available optics. The Zeta-Meter
cell was found to be better adapted to
determinations of fast settling colloids
than the horizontally oriented Briggs cell,
but less effective than the vertically
oriented Briggs cell. For high conductive
media the horizontally oriented Briggs
cell was found to be better adapted than
the Zeta-Meter. The two units together
have a capability for handling a wide
variety of industrial water and waste
coagulation problems.
65-0506
Seidel, H. Solids handling and disposal.
Water Works and Wastes Engineering,
2(9) :63. Sept. 1965.
None of the solutions to the solids
handling problem seem particularly
attractive. Anaerobic digestion of sludge is
a time-tried process which returns
valuable dividends such as combustible
gps and organic humus. whether it pays to
lime the digestor is the argument. Wet
sludpe presents dryinp and transportation
problems. Mechanical dewatering solves a
fev problems, but runs the cost upwards.
Burning of slud?e involves the digestion
question again. New high-pressure,
high-temperature incineration systems
along with atomizers, fluidizers,
polvmerizers, and devitamizers are
the present-day solution. Solids handling
is one of the most interesting, frustrating,
rewarding, costly and productive challenges
that man faces.
65-0507
Sheahan, J. P. Use of styrofoam for
trickling filter covers. In Proceedings;
20th Industrial Waste Conference, Lafayette,
Ind., May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.572-582.'
A method has been developed for enclosing
space vith a technique called 'spiral
generation' which can form singly or
doubly curved structures of rigid plastic
foam. These structures may be used as
covers over trickling filters to eliminate
such problems as freezing or acceptable
appearance. Experiments were carried out
at the Waste Water Treatment Plant,
Midland, Michigan. The effect of the cover
on the temperature of the air over the
filter was studied in Jan. to March 1965.
It was found that the air temperature inside
the covered dome was maintained at about
the same temperature as t'~>e Influent. The
outside temoerarure was as low as zero
a number of times. BOD removal was not
essentially changed for the covered filter
when compared with the uncovered filter
during cold weather. Covers for trickling
filters cannot be solely justified because
of increased efficiency. Covers do
preve-i*- freezing of the unit and, in "orthern
climates, may begin to justify the use of
covers. The covers were found not to
eliminate odors, since ventilation is
required, but they will contain the odor
release it at a higher elevation and
provide the basis for odor control with an
ozone generator. Fog was controlled
with the cover. The covers provide a
phvsical barrier to the spread of filter
flies. Two photographs illustrate the
aesthetic values of the covers. The
disadvantages are impaired air movp^ent,
lack of sunlight, and cost. The average
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Industrial Wastes
comparative costs of various types of
construction (precast pour in place,
steel, form liner, spiral generation
form, wood, space frame, spiral generation
structure) are given. The/ range from
$5.00 per sq ft for precast down to
$2.75 per sq ft for spiral generation
structure.
65-0508
Sherbeck, .1. M. Synthetic organic
floccularrs used for sludge conditioning.
Journal of the Water Pollution Control
Federation 37(8):1180-1183, Aug. 1965.
The Bay City Se^aee Treatment Works is
a primary plant treating seven mgd of
sewage and removing 1.2 tons daily of dry
solids. Conditioned sludge flows to one
of two vacuum filters. Conditioning
chemicals are added as the sludge enteT. the
mix tank. "Data compares results of
operation using synthetic organic
flocculants with using ferric chloride and
lime as conditioning chemicals. There
was an approximate increase of 40 percent
dry solids production over the years
during which ferric chloride and lime
were used. Chemical costs are reported in
a table. Trials with different synthetic
organic flocculants have reduced the
chemical cost from $14.50 to $7.00 per ton
of dry solids processed. Benefits derived
from the conversion to polymers include:
equipment savings, less floor s'-ace,
improved housekeeping, improved saf et" ,
reduced bulk of ash, large reduction in
ash handling and storage, and reduced
operating time.
65-0509
Silvester, D. K. The anaerobic digestion
of slaughterhouse waste. Institution of
Public Health Engineers, 64 (pt. 2):
100-109, Apr. 1965.
This paper concerns the problems involved
in the initial stages of the operation
of an anaerobic digestion plant for
slaughterhouse waste and the modifications
which were found necessary by operating
experience. The plant capacity was 970
hog units a day, the equivalent flow
was 37,000 gal per day, the BOD load was
1.18f' lb per day, and the BOD strength
was 3.190 pnm. All heavily pol~_',l'ed
liquors, other than blood (which was treated
separately in the coagulating plant),
were passed through a comminutor to shred
sheep paunches and other larg^, pieces of
organic mater"'-?1 and then to an agitati H
balancing tank. From there it went to the
he.iTr1 digester with the effluent being
removed diametrically opposite the inlet.
Following passage through the degassing
chamber the effluent entered the
sedimentation tank before passing to an
existing conventional plant with filter and
humus tank. The solids built up excessively
in the digester, requiring modifications.
The comminutor at the inlet was replaced
by mechanically raked screens to protect
the pum-i from odd sheep's feet. The
fine screenin,-. to remove hair and
vegetable debris is carried out over the
balancing tank, Several tables are given
of the result.', which the author describes
as encouraging. The agitation has been
increased in both the balancing and
digestion tanks to prevent quiescent
zones at the bottom of the tanks. The
plant has finally been able to produce a
burnable gas. Future developments will be
reported.
65-0510
Smith, L. L., F. H. Kramer, and J. C.
MacLeod. Effects of pulowood fibers
on fath»,->d minnows and walleye fingerlings.
Journal of the Water Pollution Control
Federation 37(1):130 -140, Jan. 1965.
The influence of short exposure" to four
tynes of wood fibers on the mortality
rate and sublethal physiological
responses with fathead minnows (Pimephales
promelas) and walleye fingerlings
(Sti"cstedion vitreum vitrr.um) was
studied. Nine tables are given which
include a summary of the bioassay
experiments, fish survival data, hematocrit
data, the effect of tricaine
methanesulfonate on the hematocrit and
amount of blood collected, and the
significance of fiber treatment in
reducing time to death at lethal
temperature. The effect of suspended wood
fibers on mortalitv of fish depends on
the species of fish, type of wood fiber,
processing method, oxygen concentration,
and. to a lesser degree, water temperature.
Conifer groundwood was the most lethal
fiber. Groundwood pulps were more lethal
than chemical pulps. There are significant
changes in the blood of fish exposed to
wood fibers. Increased hematocrit values
resulted from increased concentrations of all
grrvmdwood fibers when dissolved oxygen was
at saturation.
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0508-0514
65-0511
Smith, P. H. Pure culture studies of
methanogenic bacteria. In Proceedings; 20th
Industrial Waste Conference, Lafa'Tftc
Ind., May 4-6 1965. Purdue Univer-o'ty
Knpineerins Extension Series No. 118.
n 583-538.
Materials and methods for the Isolation
and study of methanogenic bacteria from
domestic sewage sludge are described. The
medium is given in terms of its final
percentage comDOsition The medium was
boiled to drive off dissolved oxygen and
the atmosphere above the medium was
maintained free of oxvgen by flushing with
a gas mixture of 70 percent hvdrogen and
30 percent carbon dioxide. The dilution
technique, the subculture technique,
modification of the method (to solve the
problem of culturing the bacteria by
excluding oxygen), substrate utilization
and tests for purity are briefly
summarized, These pure culture studies
are difficult because of the extre^0
sensitivity of the organisms to molecular
oxvgen. However, these organisms
can be Isolated in pure culture if
techniques are used which adequately control
the oxvgen tension at everv step in the
procedure.
65.0512
Sohr, W. H. , R. Ott. and 0. E. Albertson.
Fluidlze.d sewage sludge combustion. Water
Works and Waste Engineering, 2(9):90-93
Sept. 1965.
The East Cliff-Canitola California, sewage
treatment plant is designed to process
primary organic solids UP to an ultimate
flo« of 8 mgd, with equipment to handle
550 Ib per hr dewatered sludge. Paw
sewage enters the plant through a 4-in.
pipe and a force main, Is shredded, and
enters a clarifler where solids which
settle to the bottom are collected and
removed. The overflow enters a
chlorine-contact tank where flow is
measured, chlorine is added, and the
effluent is carried out into the Bav of
Monterey via an outfall line. Ml
solids collected from the settling
basin are oumoed to a cyclone grit
separator where noncombustible materials
are removed, and the remaining sludge is
fed into a thickener. Sludge then goes
into a high speed centrifuge where it is
dewatered enough to burn itself completely
to ash in the EluoSolids reactor Gase=
emitted are cleaner' in a liquid scrubber
and emerge as a plume of water vapor.
A small cyclone removes the ash, and it
is periodically disnosed of by landfill.
This Dorr-Oliver FS Disposal System is a
new concept in reduction of sewage solids by
ombustion. It can be operated by one
trained individual; operating costs
consist of diesel fuel, electricity, sand,
and lubricating oils. This p]ant meets all
standards set by California's air
nollution code and presents no problem to
surroxmding residents.
65-0513
Stein, J. Three years of experiments in
dehydrating sludges with the aid of
precoat filters in the purification plant,
Weldenau-Geisweid, Germany. Wasser und
Abwasser 106(50):1396 -1401, Dec. 1965.
In the purification plant, Weidenau-Geisweid,
Germany, experiments in dehydrating sludges
were conducted with Heymann and precoat
filters. A fluid free of solid particles
was achieved with the precoat filter but
not with the Heymann filter, Fifteen
experiments were performed with the
precoat filter. One determinej the
influence of drum revolutions on filter
caoacity: dehydration effect, and operating
costs. Canacity increased with the
number of revolutions; however, water
content increased too. Operating costs
did not change. Yield in solid
particles was 100 percent. Filtrate was
clear but the biochemical oxy demand
was still 100 to 120 mg per liter. The
experiment was made with activated sludge;
wood dust was used as additive (peat
dust proved to be too capillary) , but a
mixture of peat and wood dust gave
slightlv better results. When using
ash as additive, it is advantageous to mix
it with dust from grinding wood to avoid
clogginp of the filter tissue. Adding
flocculents increased filter capacity by
more than 100 percent; when fresh treated
sludge was used capacity was increased
by only 25 to 30 percent. Tables give
results of dehydration and show the
influen?.' of dehydration on filter
dimension and slrdge incineration. A
much larger filter surface is required
for dehvdrating fresh sludge than for
activated sludge, (Text German)
65-0514
Stephenson, J. W. Developments in small
scale sewage disposal. Public Health
Inspector 73(4):197-205, Jan. 1965.
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Industrial Wastes
Some brief observations on selected items
of interest to public health inspectors
who operate small-scale sewage disposal
works are presented. Many improvement'-
have been made. Their advantages are
listed: (1) fibreflass pref-V ricated
septic tanks with high impact resistance
have been developed which can easily be
handled by two men; (2) consolidation
of small town sewage systems means that
only one central plant would be needed
for several communities who would pump
sewage to it; (3) comminutors make the
task of cleaning screens and disposal
of screenings unnecessary; (4) automatic
desludgine, valves for settling tanks lessen
the problem of sludge removal; (5) mechanical
sludge removal device will extract
solids from any type of sewage; (6) filter
media produce better effluents; (7)
mechanical filter distributor features a
slow-moving distributor with a heavy
discharge which is preferable to a
faster moving distributor with slim jets;
(8) humus tanks work better on a 6-hr
basis rather than a 4-hr basis; (9)
extended aeration seems to be best suited
to the small works; and (10) portable
automatic sampling machines eliminate
the time required for individual sampling.
Other topics discussed were improved
sludgp removal and disposal methods.
recircul ~', ion of effluents, and final
purification of effluent. Local authorities
must be prepared for future modifications to
ensure greater efficiency of operation
and purification.
65-0515
Stross. R. G., F. M. Unger, J. C. Jone,,
et a]. Utilization of algae by Daphnia as
influenced by cell senescence and UV
irradiation. In Proceedings; 20th
Industrial Waste Conference, Lafayette,
Ind.. May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p.706-714.
The thoracic appendages of DaphnLa can
collect particles ranging in size from
0.9 to 18,000 cu microns from large volumes
of water. The rate of ingestion may be
in direct proportion to the volume of
particles collected by the appendages.
The utilization of senescent cells of
algae was measured and the effect of
senescent and UV-irradiated algae on the
intrinsic rates of increase of DaphnLa
populations was evaluated. The methods
and materials are described. When Daphnia
were fed suspensions of Chlamydomanas the
rate of cell removal declined with the age
of the culture. The filtering rates of
adult Daphnia pulex feeding on cells of
C. reinhardi from cultures of 10, 16
and 26 days old are shown in a graph.
Washed cells from older cultures inhibited
ingestion, although washing seemed to
remove much of the inhibition. Centrifuged
suspensions of cells from the various
aged cultures are described. The inference
that age of Chlamydomanas cultures influences
food intake was supported by growth rates
of Daphnia populations. The only population
statistic which failed to show the
influence of senescent food was the death
rate. The inhibitory effect of senescent
food was stimulated by exposure of
log-phase cell suspensions to UV
irradiation. Irradiation of food reduced
the rate of increase of the Daphnia from
the 0.28 per day observed in controls, to
0.16 per day in populations feeding on
cells given 25,000 ergs per sq mm. Larger
doses (75,000 ergs per sq mm) resulted in
only slightly greater inhibition
Associated with irradiation were
detectable quantities of lipid peroxides
in the cells of Chlamydomonas. Thus , it
was found that ingestion of Chlamydomonas
cells by Daphnia is reduced progressively
as the food cultures age. The feeding of
senescent cells of Chlamydomonas reduced
the intrinsic rate of population increase
to nearly one-third that in the control
populations. A hypothetical population was
constructed to show the influence of
algal senescence on density and permissible
washout rate of Daphnia population
in equilibrium with its food supply
650516
Synthetic textile industrv. Public
Health Service Publication No. 1320.
Washington U.S. Government Printing
Office, 1965. 23 P.
The methods of evaluating the industry's
waste load discharge and its effect on
the stream and wavs to reduce this load
in the most economical manner are
suggested. A textile finishing mill
requires from five to 15 or more gal
of water per Ib of fabric, depending op
the complexity of the finishing
process. The various operations performed
on the synthetic fibres in converting
them into a finished fabric are outlined
and a flow diagram for a mill of this
type are offered. Dyestuffs, depending on
the fibre involved, may range from ordinary
acid dyes through acetate and basic
132
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0515-0518
colors to soeclal types. The liquid
xvaste discharge will vary from about eight
to 15 tildes the weight of the fibre dves. Tn
determining disposal methods for wastes
from the manufacture of synthetic fibre
textiles . the first approach should
alwavs be a study of in-plant methods and
chemicals. More rigid processing controls
mav lead to less reprocessing and
consequently lower waste loadings. High
BOD chemicals might be replaced with lower
BOD chemicals. Excessively hot wastes
should be sent through a heat exchanger
before being discharged into a stream.
Toxic materials must be wntched; some
wi11 not be removed bv, nor interfere
with, a treatment plant hut will go
through it into the receiving streams.
Manv plants will need some degree of
treatment. Several methods are presented,
ranging from lagoons to highly complex
systems providing maximum possible
treatment.
65-0517
Teletzke, G. H. Low pressure wet air
oxidation of sewage sludge. In
Proceedings; 20th Industrial Waste
Conference, Lafayette, Ind. , May 4-6,
1965. "Purdue University Engineering
Extension Series No. 118. p.40-48.
The objective of the Zimpro sludge
treatment is to produce a sterile,
nonputrescihle solid residue, unidentifiable
as to origin, easily concentrated to the
minimum volume consistent with the lowest
total cost. Sewage sludge is heated with
air to an initiatine reaction temperature
between 300 and 400 F, then enters a
reactor where the desired oxidation and
a further temperature increase takes
place. The degree of oxidation depends on
temnerature pressure, holding time,
and concentration of the sludge received.
Operating pressures may he 150 to over
3 000 psi. If the process is not thermally
self-sustaining steam may be injected
to sustain the reaction temperature. Heat
in the oxidized products is recovered by
heat exchange with the entering sludge
and air and the gaseous effluent
separated from the liquid carrying the
solids. The exhaust gases may be scrubbed
and discharged to the air or where
economic conditions make it attractive,
mav be expanded in a power recovery unit
to recover the energy. The solids may be
separated from the carrying liquid and
concentrated bv settling sand bed
drainage, vacuum filtration, or
centrifuqation, A flo'.1 sheet is shown.
Depending on the deeree of oxidation a
wide range of end products is possible.
The drained residue is sterile and
unobjectionable after as little as 10
percent COP reduction. The relative costs
versus COD reduction are shown in a
fi >ure. The method is economical flexible,
and produces a sterile and acceptable
end product. The unit should prove
applicable for the majority of installations
in the United ^tates.
65-0518
Valente, G. \. A new idea in sludge
dewaterine. American City, 80(7):95 97,
July 1965.
After almost 3 years of operating
exnerience with a prototype sludge-dewatering
machine that operates on unconventional
hut simple principles, the City of Caldwell,
Mew Jersey, plans to incorporate this
mechanical slud?e-dewatering system in
its plant expansion program. It will
not onlv eliminate the need for sludge
drving beds, but also do away with certain
digester operating problems. The
dewatering unit consists basically of two
cells formed by a fine-mesh nylon filter
cloth th-^t travels continuously over
front and rear guide wheels, A drive
roll and sproket assembly act as a
separator between the cells. Dewatering
occurs in the first cell and cake
formation takes place in the second. A
set of center guide wheels divides the
cells into comnartments. This division
reduces the span of the filter cloth
across the cells. A flow sheet and
photograph of the unit is provided. The
operation of the unit is also described in
detail. Tests, to determine what chemicals
could be added to aid filtration and create
optimum coagulation, demonstrated
conclusively that the polve]ectrolytes
were most effective in coagulating
digested sewage sludge. Total weekly
volume of digested sludge dewatered
averaged 8,000 to 10.000 gal. Tn
comparison, sludge withdrawals onto the
drying beds have averaged 10,000 gal per
week for about 32 week per year, since
very little sludge could be placed on
the drying beds during the '''inter months
The dewatered stabilized sludge cake, which
is discharged, directly into a truck,
averages 85 percent moisture. No serious
maintenance or operating Problems have
been experienced with the unit.
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Industrial Wastes
65-0519
Varma, P. M., and R. S. Talbot. Reaction
rates of photosynthesis. In Proceedings;
20th Industrial Waste Conference. Lafayette,
Ind., May 4-6 1965. Purdue University
Engineering Extension Series No. 118.
p.146-174.
The main source of oxygen in a sewage
lagoon is from the end 'product of
photosynthesis by algae. A smaller
amount, up to about 40 Ib of oxygen per
acre per day is provided by absorption at
the air-water interface aided by wind
action. Carbon dioxide, inorganic salts,
water and energy of the sun are used by
algae to produce protoplasm with oxygen
and water released into the surrounding
medium. Since no photosynthesis occurs
at night, stabilization ponds tend to
become depleted of oxygen by the biological
demand of bacteria and other heterotrophic
microorganisms and by the algae themselves.
Septic conditions sometimes result,
Artificial illumination may alleviate this
but continuous artificial light may be
detrimental to oxygen production. Since
the rate of photosynthesis is affected
by: (1) intensity of light, (2)
pH, (3) temperature, and (4) age of the
culture, variations in these may be useful
in control. The effect of changes in
these factors on the rate of photosynthesis
of Chlamydomonas has been studied. It
was found that the rate of photosynthesis
increased with temperature at a given
pH and light intensity. Under given
conditions, there is optimum light
intensity at which the rate of
photosynthesis is maximum. Intensity of
light is more ciritical at 25 C than at
30 C. Varying other factors in experiments
is needed to establish the effect of
temperature on the rate of photosynthesis.
65-0520
Viraraghavan, T. Digesting sludge bv
aeration Water Works and Wastes
Engineering, 2(9):86-89, Sept. 1965.
Laboratory work was undertaken to
determine the suitability of sludge for
aerobic digestion under normal climatic
conditions prevailing at Madras, India.
Sludge samples were taken from a source
which receives mainly domestic sewage.
Four series of experiments involving
aerobic digestion of sludge for periods
of 5, 10, 15, and 20 days were performed.
Raw and digested sludge analyses were
carried out in accordance with the
procedure in 'Standard Methods for the
Fxamination of Water and Wastewater' (APHA)
with modifications. These were carried
out in July and August with a temperature
range of 35 to 27 C with the average
being 31 C, The conclusions reached were:
(1) A fairly high degree of digestion
of raw sewage was obtained under aerobic
conditions; (2) Aerobically digested
sludge had no disagreeable or
objectionable odor; (3) Reduction in
volatile solids depended uDon detention
time. \fter 15 days, the reduction was
not significant; (4) Nitrification of
sludge occurred during aerobic digestion;
(5) There was significant reduction
in suoernatant BOD during aerobic
digestion; and (6) Data generally
indicated that 15 days detention was
optimum for the stabilization of sludge
under the normal climatic conditions at
Madras.
65-0521
Walker J. F., and J. H. Dougherty. Use
of polyelectrolyte coagulants to enhance
settling characteristics of activated
sludge. In Proceedings; 20th Industrial
Waste Conference. Lafayette, Ind., May
4-6 1965. Purdue University Engineering
Extension Series No. 118. p.715-723.
A total of 12 different polyelectrolyte
coagulants were studied. The overall
effects of polyelectrolytes on the
BOD reaction and the oxygen utilization
rate of activated sludge mixed liquor
was examined. The effects of varying
concentrations of polyelectrolyte on the
biochemical oxidation rate were compared tc
that of a control, The data indicate
significant suppression of the BOD reaction
rate with certain of the polyelectrolyte
materials studied. Settling batch studies
were made by observation of the height
of the sludge layer versus time as the
sludge in a quiescent sample of mixed
liquor is permitted to settle. Further
studies were performed on a continuous
flow basis utilizing textile waste
waters as the source of food, After
only 24 hr of a cationic type, of
polyelectrolyte coagulant, BOD removal
efficiencies increased from 68 to
approximately 85 percent, mixed liquor
suspended solids concentrations increased
from approximately 1,000 ppm to almost
1.300 pern and the periodic system failures
previously experienced did not occur. No
one type of polyelectrolyte was found to be
universally effective in increasing the
134
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0519-0525
agglomeration and settling rate of activated
sludge The settling test performed
In a one-liter graduated cylinder using a
stirring mechanism was found to be an
effective analytical tool in the choice
of a coagulant aid.
65-0522
Wallace A. T., G. A. Rohlich and J.
R. Villemonte. The effect of inlet
conditions on oil-water separators at
Sohio's Toledo refinery. In Proceedings;
20th Industrial Waste Conference, Lafayette.
Ind., May 4-6, 1965. Purdue University
Engineering Extension Series No. 118.
p 618-625.
Two oil-water separators were studied.
These separators are part of a bank of
ten parallel basins, each receiving feed
from a common channel. Oil-water enters
an individual basin through three 18
by 18 in. slide gates operated by hand
valves located on the walkway over
the inlet end of the separators. The
effluent leaves over simple weirs at the
end of each separator and is conveyed away
in a common channel. Each basin is 80
by 18 ft in plan and has a water depth
of 7 ft 8 in Basin No. 1 has a simple
overflow weir inlet and Basin No. 2 has an
inlet consisting of four 10-in. reaction-
jets, baffles 11 in. in diameter with a
3-in. hole in the center, The basin and
inlet details are shown in figures. The
experimental method was to obtain dispersion
curves for both basins at comparable
flow rates and to measure the removal of
oil at the same time. Basin No. 2
with the reaction jet baffle inlet appeared
superior to the simple overflow weir inlet.
The testing period was brief so it would be
desirable to get more data on comparative
oil removals. Comparison between the
measured oil removals and the removals
expected if 'ideal flow' (the concept of
Camp) is assumed showed that both
separators are far from 'ideal' and that
the relative efficiencies became less
as the flow rate increased dropping from
.81 to .59 for the reaction jet baffle
and from .675 to .235 for the overflow
as the overflow rate increased from 500
to 4.000 gal per sq ft per day,
65-0523
Walters, W. R., and G. Ettelt. Dewatering
of the fly ash by-oroduct from the wet
oxidation process. In Proceedings;
20th Industrial Waste Conference
Lafayette, Ind., May 4-6. 1965. Purdue
University Engineering Extension Series
No. 118. p.551-571.
The Zimmerman wet air oxidation nrocess
(Zimnro) treats 15 to 18 percent of the
sludge produced by the Chicago Sanitary
District. The effluents from Zimpro are
now lagooned, but it may become desirable
to dewater and thicken the effluent before
transportation to the ultimate disposal
site. Sedimentation followed by sand
bed drying does not seem to be economically
feasible because of the restrictions
of winter. This paper is concerned with
two of the unit operations for solids-liquid
separation: filtration and centrifugation.
Most of the work is on filtration. The
properties Zimpro slurry are reviewed.
Bench scale filtration tests and pilot
plant filtration experiments are
described and illustrated by drawings
and photographs. A simplified sketch of
a concurrent solid bowl centrifuge is
given and oilot plant studies together
with results are reported in figures,
Dewatering the Zimpro effluent is seen as
but a preliminary step in the sludge
disposal problem. The long-term goal is
not merely disposal but use of the Zimpro
effluent in ways that will substantially
reduce costs.
65-0524
Waste from coal mine conveyed through
mountain. Refuse Removal Journal,
8(8):42-43 Aug. 1965.
The Eastern Associated Coal Corp. has
built a conveyor system for refuse
disposal at its Kopperston. West
Virginia, coal mining operation. The
refuse consists of material mixed with
the coal, such as shale and clay; the
mine handles 6,000 tons of waste products
and 12,500 tons of clean coal per day.
Refuse from the preparation plant moves
uphill by conveyor, travels through a
mountain, is discharged into a silo,
and then is dumped into a landfill.
65-0525
Wenzl, H. F. Evaporation and burning
of sulfite spent liquors. Paper Trade
Journal 149 (23):59-63 June 7, 1965.
Technical problems, processes, and technology
concerning evaporation and burning of
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Industrial Wastes
sulfite sr>"nt liquors are reviewed
with reference to the literature, Three
operations required to recover heat from
organic substances in sulfite spent
liquor are: (1) separation of liquor
from pulp with the least possible dilution;
(2) evaporation of liquor to a conceitration
which sustains combustion; and (3) burning
of concentrated liquor with as complete
recovery as possible of heat from
combustion gases. Several commercial
processes available for evaporation,
'jhich is normally carried to a solids
content of 55 percent, include multiple
effect vacuum evaporation, back pressure
evaporation, and cvanoration by thermal
comnressi on . Tables o.ive a comparison of
heat consurntion and fuel savings for
different evaporation systems, and a
survey of fuel and power consumption for
a sulfite puln mi]], with and without
alcoho] production, for naner anc for
dissolving pulps utilizing various methods
of evanoration. The three evaporation
systems are also compared bv means of
flow diagrams. The vacuum system and the
counter pressure system can be combined
with alcohol qtripninp to reduce the
size of the plant and increase safety of
operation. Another table gives data which
shows that sulfur losses in the condensate,
in the waste stream of the six-effect
evaporator and in the waste gas, increase
with increasing temperature and decreasing
pH of the liquor. The combustion of the
concentrated spent Hquor is discussed. Wet
combustion (or flameless oxidation),
where completely different considerations
have led to snent liquor recovery, is
discussed. Heat production from sulphite
spent liquor in relation to dry content
and evanoration system used is presented
graphically,
65-0526
wet oxidation of sewage sludge. Vater
and Waste Treatment Journal, 10(9):477-478,
Sept.-Oct. 1965.
Summaries are given of a research paper
on the wet oxidation of sewage sludge,
a report on the operation of a wet
oxidation plant in Westchester County,
New York, and the regulations recently
issued in Britain covering wet oxidation
plants. In the research paper by Hurwitz,
Teletzke, and Gitchel, the characteristics
of various degrees of oxidation of a raw
primary sludge, a digested primary-
activated sludge and a concentrated raw
activated sludge are discussed. S0lids
from low to high degrees of oxidation
show qualities such as sterility,
biological stability, set tleabili ty . and
drainability , which make the erd-products
suitable for ultimate disposal. An
installation at Blind Brook in New York
has a wet air oxidation process wi th a
capacity of 1 ton per day which has been
in operation for a year. In the wet air
oxidation the oxygen in the air under
greater than atmospheric pressure combines
with the organic material in organic
solution or suspension at temperatures
below 372 C. At a treatment cost of $41
a ton, it was concluded that the wet
oxidation process was an economical
solution to sludge handling for small
plants. Circulars issued by the
Ministry of Housing and Local Government
and the Secretary of State for Wales
contain technical data on aeration sludge
plants including a description of the process,
recommendations on sites, sewage flow.
general requirements, and basic design
criteria. The issuance on these bulletins
appear to give approval for use of this
type of equipment in Britain.
65-0527
Woodland R. G., M. C. Hall, and R. K.
Russel]. Process for disposal of
chlorinated organic residues. Journal
of the Air Pollution Control Association,
15(2):56-8, Feb. 1965.
A continuous process for the disposal of
halogen-containing organic residues is
described together with a schematic
drawing and two photographs which show
the decomposition of wastes to gaseous
byproducts by high temperature reactions
with air and steam. The exit gases ,
essentially carbon dioxide, nitrogen,
and hydrogen halides can be scrubbed with
water to remove any atmospheric pollutant.
The rate of residue generation of this
type is estimated at over 1,000 tons a
day in the United States. The residues are
pumped from storage tanks to the reactor
where a reaction with steam and air takes
place at 900 to 1,400 C to convert the
haloeenated hydrocarbons to HC1 and carbon
dioxide. After cooling in a carbon
block, direct contact cooler to 100 C,
the gases are passed through a carbon block
scrubber to remove the potential air
contaminants such as HC1. After passing
an entrainment senarator, the remaining
components (nitrogen, oxygen, water
vapor, and carbon dioxide) are vented to
the atmosphere. Organic S compounds would
136
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0526-0530
give sulphur dioxide in the exit gas. Tables
are given of the chemical reactions
involved, the operating conditions, and
the residue composition. This process gives
emission products such as HCL which are less
obnoxious and easier to absorb than the
chlorine which results from low temperature
incineration. The approximate cost of a
unit capable of disposing of 20 million
Ib per year of highly chlorinated
residue has been estimated at $250,000. At
the Hooker Chemical Corp. at Niagara
Falls, the direct costs of reactor disposal
are less than 50 percent of the direct
costs for drum burial. This cheaper than
conventional method (i.e. ground burial) also
provides complete and permanent disposal.
65-0&28
woodl«?y, R. A., and S. L. Moore. Pollution
control for mining and processing of
Indiana coal. In Proceedings; 20th
Industrial Waste Conference, Lafayette.
Ind., May 4-6, 1965. Purdue University
Fngineerlng Extension Series \To. 118.
p.265-274.
Coal mining is the leadino mineral
industry in Indiana. Pollution from
surface mines, underground mines, and coal
processing plants is being controlled by:
flooding final surface mine excavations,
diversion of run-off from active mine
operations, rapid conveyance of
precipitation and seepage waters from
mining operations, disposal of acid'
producing refuse in surface mine excavations,
clarification of coal wash water in
settling ponds, reuse of coal wash waters,
and soil coverage of acid-producing
refuse disposal sites and roads. The
history of coal mining in Indiana is
traced. As early as 1925, water pollution
from mine drainage to lands by surface mining
operations was observed. The various control
measures adopted are reported. Graphs
show: the annual coal production in
Indiana the number of active coal mines
in Indiana the annual acreage disrupted and
reclaimed and the stream mines affected
by mine drainage. When a surface mine
is opened all surface streams around
the coal recovery area must be diverted.
Diversion ditches should be utilized.
Acid-nroducing material should be deposited
in an excavation that will be covered
with cast overburden during coal recovery.
Generally, the underground mine drainage
problem in Indiana is confirmed to disposal of
seepage water from active workings. The
disposal of acid-producing material from the
processing plant is a major problem. Most
pollution problems due to mine drainage in
Indiana can be controlled. Adequate
pollution control for acid sandstone
overburden has not been established and
research is needed
65-0529
Voods C. Determination of proteins in
waste water. In Proceedings; 20th
Industrial Waste Conference Lafayette,
Ind., May 4-6, 1965. Purdue University
Fngineering Extension Series No. 118.
p.501-515.
Three methods for the determination of
proteins (Kjeldahl, Folin reaction, and
Riuret reaction) are described ir. detail.
Data for dilution factors of 25 to 200
on samples of digested anaerobic sludge
taken from the El Paso Treatment Plant are
given in figures. The variation in the
results is more likely due to the actual
variation in the samples than the dilution
factor The results are more accurate
if the dilutions are such that the optical
density falls between 0.4 and 1.8. Typical
results of determinations of proteins
by the three methods are tabulated. The
wastes studied included: feed sludge,
transfer sludge from first to second
stage supernatant from second stage,
and stabilized sludge from second stage,
all from a two stage digestor operated by
the City of Fort Worth, Texas; raw primary
sludge, and digested sludge from another
plant operated by the City of Forth Worth;
slaughter house wastes from near El Paso.
These data show a wide variation in
numerical values of the protein concentrations
for the three methods. None of the methods
can be considered to give an 'absolute
value' of protein concentration for
eacb method has its limitations. The
values gotten with the Fjeldahl techni'nue
are probably nearer the absolute value
because of the tendencv to have a low
result due to the lower nitrocen content
of conjugated proteins is offset bv the
fact that not all organic nitrogen
is associated with protein.
65-0530
Zlmpe], J. Elimination of waste water.
VDI (Verein Deutscher Ingenieur)
Zeitschrift, 107 (14):645-647 , May 1965.
Twenty-four articles and books published
in 1963 to 1964 in the area of waste water
137
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Hazardous Wastes
technology are reviewed. Since October
1, 1964, the law prohibits the use of
'hard' detergents. Soft detergents are
more easily decomposed by bacteria but
are more poisonous to fish. The increased
atrophy of many lakes necessitates a
third cleaning staee for the wa^te water.
There the nhosphates and nitrates are
either biological!v hound bv a];'ae
or chemical!v precipitated. Phosphates
can be hound ~->v aluminum, conner, iron or
magnesium salts, nitrates bv iron
hydroxide. Digested sludge has onl^T one
third of the volume of non-dipestpd sluHpe.
Its elimination is therefore up to 77
percent less expensive. Natural dr^inp of
sludge is less expensive than artificial
drying in vacuum filters. Larce cities
incinerate their sewage sludge0. The
least expensive (5.07 DM ner cu m) method
is the combination of centrifuge + vacuum
filter + incineration. A new method is the
wet oxidation of the Zimmermann process.
More and more sewage plants are becoming
automated, however, only cities with a
population above 100,000 can afford the
investments in automated measuring
and control equipment. Smaller cities can
participate in regional cooperative
programs to supervise sewage treatment
facilities. (Text-German)
HAZARDOUS WASTES (including
Pesticides)
65-0531
Breidenbach. A. W. Pesticide residues in air
and water. Archives of Fnvironmental Health,
10:827-830, June 1965.
The level of contamination of surface water
bv a pesticide which will interfere with any
of the industrial or domestic uses of water
is not generalIv known. Concentrations which
might be deemed accentable for one use would
not be for another use. Contamination studies
began in 1957 hv the U.S. Public Health
Service. Samples from rivers and lakes are
obtained to identifv the organic chemicals.
using the carbon adsorption method. Since
1962, the aromatic fraction of the chloroform
extract of these samples has been subjected
to electron caoture gas chromatographv which
supplemented an infrared analysis, and was
later exposed to microcoulometric titration
pas chromatography. The laboratory is
currently able to detect several pesticides--
DDT, DDE, Aldrin, and heptachlor included--and
some organic phosphorus type pesticides.
Pesticide data is entered into the STORE!
system of storage and retrieval by electronic
data processing equipment. An accurate
assessment of pesticide concentrations in
ambient air cannot be made at this time.
Techniques are currently being worked out to
identify pesticides in the air, but data
available is not sufficient to fully evaluate
its aualitv to date.
65-0532
Kawahara, V. K. and A. I-7. Breidenbach.
Pesticides and water quality-potentials for
their removal. Columbus, Ohio, U.S. Public
Health Service, "965. Nov. 3, 1965. 10 p
An efficient sampling system for determining
the presence of pesticides requires the
passage of 250 gal of water on activated
carbon at a flow rate of 100 ml per minute.
One can confirm the presence of some pesticides
bv injecting aliauots into gas chromatographic
equipment or by subjecting them to infrared
spectrophometric examination. The second
type of sample is basically a bottled sample,
one liter in volume. The pesticides on the
silica gel layers are removed. Analysis is
accomplished with the electron capture and
microcoulometric gas chromatographic equipment.
The results of two studies in 1967 and 1964
indicate the presence of chlorinated bvdrocarhon
nesticides in rather low concentrations in
surface waters. But fish, are more sensitive
than man and many have been killed. Tt was
concluded that intermittent oneration of
carbon columns will reduce soluble organic
material in clarified bio-oxidized waste
effluents to levels below 1 mp; per liter.
Solubility of the particular pesticide in
water plavs an important role in its removal
by coagulation and filtration through sand.
DDT was easily removed this way. Using ozone
and potassium permanganate did not decrease
chlorinated hydrocarbons. Foaming of secondary
effluent removed 35 nercent of organic and
75 percent of synthetic contaminants. Single
pass electro-dialysis reduced salt concentration
by 45 percent. Oxidation may eliminate organic
contaminants.
650533
Manual for decontamination and disposal of
empty pesticide containers. Washington,
National Agricultural Chemicals Association,
June 1965. 20 p.
Pesticide containers are classified combustible,
larw non-combustible, and small non-combustible
Each of these containers should be disposed
138
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0531-0537
of as auic'Ov as possible. Combustible
containers can be completely destroyed by
burninc. If burning is not possible, tbe
containers should be crushed and buried. Weed
killer containers should not be burned. Small
nor combustible containers are of sizes up
to tbe 5 gal size. Tbev should not be reused
for anv purpose. The inside should be
"ashed i.n t h water containing a determent and
caustic soda and tbe water buried. Class and
plastic containers should be completely
mutilated and metal ones crushed. Burying in
dumps is their method of disposal. Large
non combustible containers are 15 to 30, or
55 gal metal containers. These containers
should be decontaminated bv a professional
drum reconditioner, If this is not possible,
the container should be mutilated bv puncturing
and then burned. Some professional methods of
decontamination are washing, heating, and
sandblasting. Different methods of
decontamination are used for different pesticides.
t"o groups: those decomposed bv alkalies and
tbose hv an acid condition. The physical state
of wnqte material from formulation production
mav be in several forms: solids (wettahle
powders dust concentrates, diluted dusts);
liquids (oil solutions emulsifiable
concentrates); and gaseous (true vapors, air
dispersed mists). Solids may be disposed by
removal and buried in a designated area; may
be flushed down sewers if the system is equipped
for the decontamination of toxic materials;
may be placed in a permanent waste stock pile
which meets all air and vater pollution
requirements; and may be sent to a solid
settling pond if such hydrocarbon are de-toxified
either before or after entering the pond. As
to liquid disposal, tbe solutions must not be
run into sewers, laaoons or placed on solid
waste piles. It is recommended tbev be burned
in an incinerator. As to gaseous disposal, the
vapors or mists mav be removed hv suitable
scrubbing towers and or activated carbon
towers. Scrubbing liquids can be sent
periodically to ponds for decontamination.
65-0534
Manual on waste disposal. Washington,
National Agricultural Chemicals Association,
June 1065. 44 p.
A special NAO -Tndustrv committee issued a
series of suggestions to be used as
guidelines which micrbt be followed in the
disposal of waste from pesticide manufacturing
and formulating operations. These guidelines
are not intended to supercede any effective
waste disposal practices now currently followed
bv individual plants. Most pesticides present
problems in waste disposal. Among some of the
items covered are: pollution control; waste
prevention; general disposal methods; specific
methods of waste treatment and disposal;
burial method; incineration; deep well
disposal; disposal at sea; disposal methods
for chlorinated hydrocarbons, organic
phosphates, and related materials; and disposal
methods for carbamate pesticides, dithiocarbamates
phenoxy acids, salts and ester, botanicals
and inorganic pesticides. Diagrams, charts,
land layouts, and bibliographies are included.
650536
National Agricultural Chemicals Association,
Specific methods of waste treatment and
disposal--burial. In Manual on waste disposal.
Washington, June 1965. p.15-17.
Considerations given to the burial of solids
and trash should be based on: sanitation
requirements; availabilitv of land; pollution
potential to surface or ground water supplies;
choice of the trench method or the area method;
and operating a land fill as an engineering
project. Burial should not he adopted for
the disposal of waste unless: the landfill
operation will not pollute water sunplv; tbe
method is economical and does not lead to loss
of materials which should be salvaged; the
phvsical properties can be compressed; there
is sufficient quantity to attain maximum
economy; adequate land is available; the
ultimate use of the land will benefit from tbp
fill operation.
65-0535
National Agricultural Chemicals Association.
Disposal methods for chlorinated hydrocarbons.
In Manual on waste disposal. Washington, June
P.?7 ?Q.
Chlorinate^ hvdrocarbon pesticides from a
decontamination standpoint are divided into
65-0537
National Agricultural Chemicals Association.
Specific methods of waste treatment and
disposal--incineration. In Manual on waste
disposal. Washington, June 1965. p.17-23,
Prior to incineration the physical and
chemical proportions of the wastes must be
139
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Salvaging
determined. Proper burning of waste liquid
requires proner mixture of air and atomization
of the licmid. Furnace and burner selection
sbould be done with care. The selection of
solid waste burners can also involve complex
considerations. Pome tvpes of incinerators
are: trench incinerator (used to destroy
chemical wastes and containers), orpam'c liquid
waste burner (to handle waste solvent disposal),
and chlorinated hydrocarbon disposal svstem
(for tar and waste solvents) The disposal of
chlorine-containing tars and waste =o]vents
poses a particular problem to the pesticide
manufacturer. Such tars and solvents cannot
be buried in any significant amount and when
burned in simple pits and furnaces, hvdtogen
chloride gas and smoke can cause air pollution.
A residue (tar) disposal system is illustrated
which, although expensive to buy and to operate,
does provide a positive, safe means of burning
such material.
65-0538
Weaver, L., C. Gurnerson, A. Breidenhach. et al.
Chlorinated hydrocarbon pesticides in major
U.S. river basins. Public Health Reports,
80(6):4S1 -493, June 1965.
Fxtensive surveillance for chlorinated
hydrocarbon pesticides as well as other
synthetic orpam'c pollutants has been underway
hv the U .<*. Public Health Service for several
years. Recent development of analytical
procedures capable of measuring pesticides in
the parts-ner-trillion ranee on erah samples
made it desirable to conduct a special
synoptic survey of various U . S river systems
during September, 1964. Two 1 quart grah
samples were collected from each of 96
different sampling points. Three types of
analytical procedures were employed: (1)
liquid liquid extraction, (2) thin layer
chromatography, and (3) microcoulometric
titration gas chromatopraphy. In order of
frequency of occurrence, dieldrin, endrin,
DDT, and DDF were found in all major river
basins. Heptachlor and aldrin were less
abundant. DDD was detected at only one
sampling station: presumptive evidence of
benzene hexachlorine was observed at onlv
one station; and no indication of heptachlor
epoxidp was seen at anv station. These three
-results may have been due to the lower
sensitivity of the procedure for the three
compounds. Generally, both the occurrences
and concentrations found in grab samples from
tbe synoptic survey were in accord with the
results of previous analyses of samples
obtained bv the carbon absorption method.
SALVAGING
650539
Accent on technology. Waste Trade World,
106(18) :13, 14, May 1 . 1965.
Several displays at the International Trade
Center of the London International Engineering
Exhibition are described. The Hiab
Speedloader, a versatile crane exhibited by
tbe mechanical handling department of George
Cohen Machinery Ltd., is available in a range
of models and can be fitted to most types of
lorries. Copies of an article, 'Cutting lorry
loading costs' which was printed in Waste
Trade World and which describes their use,
were available. The Crane Weigher, perhaps
suitable for merchants without weighbridge
facilities, is described. It allows direct
weight readings to be made at the time the
metal is being lifted. A range of compact,
box-girder desigped cranes, characterized bv
high performance and low price, were displayed
hv Acrow Ltd. Two types one all-electric in
oneration and offering spans UP to 55 ft, are
described. A ran^e of electric hoists was
shown and technical data, including load
capacities, lifting heights, sneeds, direction,
control, etc., were supplied.
65-0540
Air Pollution Control Association. TI-5
Public Utilities Committee. Informative air
pollution problems in fly ash sintering plant.
Informative Report No. 6. Journal of the
Air Pollution Control Association, 15(3):123-124,
Mar. 1965.
In 1962, the fly ash collected from pulverized
coal-fired boilers in the United States was 11
million tons, of which 400,000 tons were
collected at Con Fdison plants with a disposal
cost of $1.50 a ton. The only known application
that has potential for keeping abreast of
production (25 million tons in 1980) is used
as a lightweight aggregate for concrete when
sintered at 2300 F after pelletizing into
balls with a maximum diameter of 0.75 in.
The Con Kdison Astoria plant with a 1.010 ton
per day capacity feeds the raw fly ash from
storage to pelletizers and thence to the
sintering grates. The sintered fly ash cake
is broken up and conveyed to storage piles
after screening to remove the fines. The
chief difficulty appeared to be excessive dust
formation. Lack of control on the sintering
operation resulted in a drying, rather than
sintering, of the pellets which resulted in
the emission of clouds of dust, Proper control
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0538-0544
of tl'e sintering operation eliminated this
problem. It was found that the conveying of
fly ash by open belts created dust, therefore
open belts are being replaced by enclosed
conveyors as rapidly as possible. In the
interim, water sprays are being used at
strategic points. In general, the dust
problem arose at transfer points which were
insufficiently exhausted. In two years the
nuisance dust problems have been corrected
and the installation is considered a success.
It was anticipated that the combustion
air nulled through the burning zone might have
an excessive dust load, but it was found that
no dust collector was needed. This report
represents the 'best thinking' on thp sintering
of flv ash of the Air Pollution Control
Association.
65-0541
Aluminum scran recoverv advanced with
induction furnace. Industrial Heatine,
32(7):1258, 1260, July 1965.
An aluminum scran melting operation, which
melts and recovers saw chips, scalpings, and
other finely divided scrap, is described.
A sixtv cycle, 700-KW, 7 000 Ib coreless
induction melting furnace is used. Scrap
from aluminum fabricating and rolling operations
is separated by alloy and charged in batches.
The electromagnetic stirring action, inherent
in an induction furnace, thoroughly mixes
the metal and brings slag and other impurities
to the top of the melt. Homogeneity of the
melt prevents alloy segregation and keeps
gases and inclusions to a minimum, resulting
in the recovery of metal of excellent quality.
Molten aluminum is poured into sows and
subsequently remelted for rolling mill slabs.
The furnace, which requires little floor space,
can melt 3,000 to 3,100 Ib of aluminum per hr.
It is simple to onerate and does not require
skilled labor. Maintenance is minimal with
lining life expected to exceed one vear.
65-0542
Bender R. J. More intensive utilization of
flyasb. Power, 109 (6):94 June 1965.
Mr. A. Jarrige, chief engineer of Mines of the
North and Pas de Calais, France, whose
company intends to build a plant designed to
make light aggregate with sintered flyash
pellets, spent over four weeks in the U.S.
studying the development of flyash utilization.
He feels that although flyash has many
applications, it is difficult to convince people
to use it. His visit culminated in a recent
Power-sponsored conference in New York, where
he reviewed his findings. From the discussion,
six facts clearly emerged: (1) A great amount
of research on the properties and potential
uses of flyash is being carried out in the
United States, although more coordinated
effort is needed; (2) The valuable assets of
flvash are known to those in research, but
not enough is being done to pass the
information along to those who could nrofit
bv it; (3) Ffforts should be made to
understand the effect of slight differences in
the nhvsicfl and chemical comnosition of
flvash and to recommend appropriate ways of
conino with them; (4) Although a substantial
amount of flvash is used by those who nroduce
it, little effort is made to facilitate its
sale and transnortation; (5) The use of
Portland cement, which in Europe contains 25
percent flvash, is being used at an increased
rate for road construction in France, and
various applications are spreading to other
countries; and (6) a coordinating body in the
United States would be very useful, sponsored
bv one of the electrical utilities since they
are the major flyash producers.
650543
Bevan. R. E. Refuse analysis-recent tests in
Manchester. Public Cleansing, 55(1) .-33-36,
Jan. 1%5.
Three tables, with no discussions or conclusions,
reveal the economics of a separate waste paper
collection and the refuse storage capacity
required if it were practical to collect
waste paper senaratelv, One table contains
an analysis of a load of household refuse not
including a separate paper collection, and
the third composites the first two. One
hundred and ninety-eight homes were selected,
but only 109 pan<=r sacks of separate waste
paper were collected. Seven hundred and
eighteen Ib of paper were collected separtely
with 10 Ib of contraries. Eight hundred and
forty Ib of the 2,720 Ib of regular bin
collection was unseparated waste paper.
65-0544
Big municipal collection drive in Scotland.
Waste Trade World, 106(U):11. Apr. 3, 1%5.
A i2,500,000 expansion of a plasterboard liner
plant at Mug]emoss, Aberdeen, Scotland, now
being completed will not onlv furnish a needed
product, hut will double the present consumption
of 900 to 1,000 tons per week of waste paper
valued at fcSOO,000 per vear. The local
municipal authorities in Scotland and North
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Salvaging
of England, whfo presently supply much of the
waste paper, have indicated that they will
make an effort to increase deliveries to meet
the new demand which should net fc1,000,000 in
the next year. In Scotland the main sources of
waste paper are the larger cities, such as
Glasgow, which receives fc100,000 a year for
1,000 tons per month of waste paper. Edinburgh
furnishes 500 tons a month, Aberdeen 200 tons.
and Dundee 60 tons. This new demand should
stimulate municipal waste paper collection in
Scotland.
65-0545
'Bricks' from shale. Waste Trade World,
107(17):11 , Oct. 23, 1%5.
A new process of producing lightweight aggregate
building blocks from bituminous shale, clav
or volatile ashes has been developed in
Poland. Since the process makes use of waste
material with some coal content, additional
fuel is not reauired, which lowers the
production costs. It is claimed that the
Polish method is the cheapest method available.
The concrete has better thermal insulation
properties and the lowering of the per unit
weight has not resulted in any lessening of
its wear and tear qualities. Furthermore, the
overall weight of a building whUch utilizes
this concrete can be cut by 20 percent and
the use of steel for reinforcement by 10 to
15 percent.
65-0546
C. C. Cooper install bulk-Handling plant for
scrap. Waste Trade World, 107(2):6, July 10,
1965.
A recently-installed bulk-handling plant for
scrap with automatic bale conveyancing for
the rapid loading of rail wagons is described.
The plant, situated under a laree gantry crane,
is mounted on a raised platform with access bv
a concrete ramp. A baling press is DOsitioned
under the platform at the rear from which the
finished material is conveyed directly to
railway cars. At present throughput averages
around 200 tons per week, but increased
production is expected. The operation is
fast, compact, and efficient, enabling the
firm to handle laree quantities of a bulky.
comparatively lightweight commodity Scrap
intakes are derived mainly from works clearance
and demolition contracts. Finding new outlets
for processed scrap is the biggest problem
facing all merchants, but the use of a modern
and efficient transport system for scrap
collection has enabled the firm to extend its
sphere of operations. Other items of equipment
at the yard include a Hyster 10-ton fork-lift
truck, a Jones 4-ton crane, and scrap shears.
65-0547
Con Ed turns waste to wealth at fly ash
sintering plant. Rock Products, 68(10):81-82,
Oct. 1965.
The process and equipment used at the 1,000-tpd
fly ash sintering plant at the Astoria (L.I.,
N.Y.) Generating Station of the Consolidated
Edison Co.. whttch converts fly ash into
lightweight aggregates used in structural
grade concrete, is described and illustrated.
Fly ash collected bv electrostatic precipitators
is pelleti zed and conveyed to a sintering
machine whtich uses a Dwight-Lloyd type of
traveling grate. Carbon content of the raw
flv ash from the Astoria Station usually ranges
between 6 and 8 percent, with a minimum
content of 4 percent This provides enough
combustible material for self-ignition when
subjected to the ignition burner flame.
Consumption of natural gas used for firing is
about 1,200 cu ft per ton of sintered material.
Operations are regulated from a central
control console. The suppliers of major
equipment used in the process are listed.
65-0548
'Dumpster' enters the scrap trade. Waste
Trade World. 107(17):8, Oct. 23, 1965.
The Demps ter-Dumt>st er containerized handling
equinment made by Powell Duffryn Engineering
Co. Ltd.. of Cardiff, goes to work in the scrap
Iron and stee] trade with significant benefits
for both the onerators and their clients. The
big canacitv Dempster-Dinosaur system is
already widelv used in the scrap iron and
stee] business but now a substantial order
from Birmingham merchants N. Perks Ltd. marks
the Duiroster's entry to the trade. Perks are
beine supplied with tilt type demountable
containers of 6-cu yd capacity and Dumpster
303 C handling units mounted on Bedford KGT
chassis. They chose the Dumpster instead of
the Dinosaur because of the lighter system's
ability to operate in small, congested
scrapyards with narrow accesses and the
handling unit's high maneuverability made
possible by the short wheel-base chassis.
The Dempster-Dumpster scrap handling container
system is already in use by Perks and their
new service is growing rapidly in the
Birmingham area.
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0545-0552
650549
Ervthropel, H, Ash and slag.
Brennstoff-Naerme Kraft. 17(4):191, Apr. 1965.
The enormous amounts of ash and slag produced
bv lar?e, coal-heated, power stations pose a
real utilization and disposal prohlem.
Therefore all German, French, and British
literature has been scanned and the articles
pertaining to this problem have been listed.
(Text German)
65-0550
Fussell, 0. P. Selection and use of secondary
fibers in cylinder board manufacturing. Paper
Trade Journal, 149(49):78-81 , Dec. 6, 1965.
The changing patterns of waste paper salvage
are discussed. Control of contaminants and
new methods of contaminant removal, including
asphalt dispersion, cylinder board deinking,
and plastics and wax removal, are described.
Asphalt dispersion is a thermo-mechanical
process which disperses asphalt, waxes, pitch,
sizes, and wet strength resins to produce a
sterile, deodorized product worth $15 per ton
more than the raw materials, which consist
mainly of old corrugated boxes and some cylinder
board filler stock. Deinking, used on printed
news as well as highest white grades, performs
the functions of pulping, cooking, cleaning,
screening, and bleaching. A cylinder board
mill batch deinking system, which pulps raw
materials at elevated temperatures of about
120 F, is described. The separation of
polyethylene type plastics and fibers is an
operation of extremely selective discharge
pulping, followed bv particle size screening.
Most of the raw material is milk carton and
cup stock. Heavily waxed stock goes mostly
to export markets where wax salvage is a
factor along with the need for secondary fiber.
Molded pulp products are an outlet for lightly
waxed waste, which is decreasing in supply.
The asphalt dispersion, deinking, and plastics
removal systems are presented in flowsheets .
The problems between waste paper dealers and
the mills are discussed.
65-0551
Goodeve, C. F. Research on scrap. Waste
Trade World, 107(7):7-9, Aug. U, 1965.
Since scrap iron is an important source of
raw material for the expanding British steel
industry, experiments were conducted to
improve its conversion to steel. By 1966
open-hearth production is expected to decrease
to less than two-thirds of the total while
the new oxygen steelmaking processes, LD,
LD-AC, Kaldo and Rotor should exceed a
quarter. Since the increasing cost of
electricity is a major concern, a half-ton
electric arc furnace was converted to an
oxy-fuel steelmaking unit by replacine the
three electrodes with a sincle central burner
and by installing a waste gas extraction
system to give the benefit of a water-cooled
damper to control furnace pressure. It was
established that rimminfi, carbon and low alloy
steels could be made with good control of
carbon and sulfur to within normal
specifications. The same results were obtained
with larger plants. The fuel oxygen scrap
process also has the advantage of lending
itself to fumeless refining. To improve
charging techniques, it is important to
increase bulk density in the charging boxes.
Density experiments showed that the charging
box should be as large as possible and that
hydraulic shearing offers the most attractive
way of increasing scrap density. Mechanical
charging devices are in the process of
development.
65-0552
Goodeve, C. F. Research on scrap - part IT.
Waste Trade World, 107(8):6-«, Aug. 21, 1965.
Mechanical charpins devices for steel plant
furnaces are reviewed. The only known rapid
charging system for open-hearth furnaces is
described. The basis of the system, whb'cb has
already charged 85,000 tons of material into
a 200-ton tilting furnace, is a wheeled scrap
bin hauled bv a Tuemaster tractor. This
techniaue. plus the experimental use of
oxy-fuel roof burners has shortened tap-to-tap
times by about one-third, with considerable
reduction in fuel consumption. The capacity
of 5 larger bins, now under construction,
will be 27,000 cu ft to allow 125 tons of
cold material to be charged and scrap
consumption to be increased. Calderon chargers
for oxygen converters and open-hearth furnaces
consist of a wide gauge railway carriage on
which is mounted an 'orientating' chute and a
mechanism for tilting the large container of
scrap. Twenty-two tons of scrap can be
charged into a 75-ton vessel in a few minutes.
The system has also been adapted for charging
scrap to fixed onen-hearth furnaces. Scrap
charging at a new electric arc steel-making
plant where wagons, instead of the usual
magnet crane, are used is described. Discussion
of additional aspects of scrap handling
includes assisted meltinc of scrap, operational
research into problems of handling and charging
scrap, the regional pattern of supply and
demand, procress within the scrap industry,
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Salvaging
and technical cooperatton. The importance of
research on scrap and the development of
improved techrti CIUPS for handling and
reprocessing scran are stressed.
65-0553
The inside story on waste paper. Public
Cleansing, 55(12):689 Dec. 1965.
It has been calculated that in 1964 waste
paper recovery saved Great Britain approximately
60 million pounds in terms of wood pulp which
would otherwise have to be imported. Local
government officials have been wary of Che
argument that recovery of waste paper conserves
tipping space and reduces costly disposal
operations. I-cwever, the volume of paper is
increasing and is beginning to justify its
separate collection and disposal. In relation
to the national economy, there is little doubt
as to the merit of salvaging waste naper.
65-0554
Klass, C, P. Deinking--an art reaches to
become a science. Paper Trade Journal,
149(42):46-49, Oct. 18 1Q65.
Papers presented at the 10th Annual Deinking
Conference held on Oct 6 to 8, 1965 in
Boston are reviewed. The highlight of the
two-day meeting was a description of the 25
tpd unique flotation deinking system, which
has been in operation at Kimberly-Clark''s
Niagara Falls, New York mill since April, 1965.
Other papers presented include: (1) a
preliminary report on the effect of cooking
variables on the properties of deinking fibers;
(2) the dyeing of secondary fibers; (3)
sizing of secondarv fibers; (4) a comparison
of the physical and optical properties of
unbeaten deinked pulps and virgin pulps; (5)
the functions of surfactants in deinking; (6)
a comparative study of the physical properties
of pulns made from rags, linters and cottom
linters; (7) the effects of bleaching by
various methods on the physical characteristics
of ceinked pulps; (8) the importance of
quality water in a secondary fiber Trill; and
(9) a description of an ideal deinking flow
diagram. The meeting ended with a pane!
discussion on the problems encountered in the
use of serondarv fibers and panelists offered
their thoughts about the future of deinking.
65-0555
Load cells speed scrap gathering. I>aste
Trade World, 107(3):7, July 17, 1965.
The Martin-Decker tension load cell completely
eliminates the need for a fixed central weighing
station. Scrap is now gathered from all points
in the yard then carried directlv to the
charging cupola while being weighed en route.
This practice of weighing, while loading or
^atherin", hv-nasses the wasteful and
time-consuming stopover at a fixed location
scale. The size and shape of scrap is often
deceiving, and needless trips to and from the
charging cupola are saved bv weighinp while
loading. Charging time is cut also, because
optimum charge is ensured every time. Easily
installed, the load cell eliminates guesswork
on the part of the lift truck operator. Tension
or compression models are available.
65-0556
Waslova, L. G. Biosynthesis of vitamin B12
in methane, fermentation. Washington, U.S.
Army Foreign Science and Technology Center,
I965. 5 p-
Fermentation industry by-products are utilized
to produce vitamin B twelve hv thermophilic
methane fermentation. Industrial methane
fermentation is carried out with a mixed
culture of bacteria which allows the use of
nutritive and nonnutritive waste products as
nutrient media, Fxperiments were carried out
to produce B twelve from potato starch
production by-products. Fesnlts showed that
a necessary condition for the fermentation of
the bv-products of potato starch production
is the maintenance of the ratio between
carbon anc nitrogen in the substrate within
limits of 10 to 1n;1. The addition of cobalt
salts increases the vLeld of vitamin B
twelve threefold.
65-0557
Misra, D. K. Indian mill produces printing
papers from bagasse pulp. Paper Trade
Journal, 149(17):47-A9 , Apr. 26, 1965.
Paper with 100 percent bagasse pulp was
produced at the Mandya National Paper Mills
of Belagula, India. Mandya maintains a Horkel
depitMng station at a sugar mill 26 miles
distant, where 65 to 70 percent of the pith
is removed from the bagasse. The nith is
combined with unexchaneed bagasse and is
hurned in the sugar mill's bagasse-fired
steam boiler, Twenty percent drv bagasse is
obtained bv further upgrading at the pulp mill
by another wet denithing system. This bagasse
is digested in a Black Clawson Pandia continuous
digestion syste™ and enters the cooking zone
containing a residual pith of 4 to 5 percent.
144
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0553-0560
Tt is cooked for 10 to 12 minutes at a stea^
pressure of 110 psi. and free residual alkali
in the black liquor is maintained between 8
to 10 gpl, producing unbleached screened pulp
in 50 percent yield. The pulp is bleached in
a three-stase bleachery employing a chlorination
caustic extractiop and calcium hvpochlorite
sequence. It has a C,. E. brightness of 80
and a TAPPI viscosity of 40.0 cp with a
pentosans content of 23 percent and 77
percent cellulose. After passing through one
hydrafiner and one Jordan the stock freeness
is developed to 40 to 45 SR and is then
processed in a paper machine with a 138 in.
wide wire and a wire length of 85 ft 4 in.
Data on the bulk, burst factor, tensile
strength, breaking length, tear factor, and
double fold is given for 100 percent bagasse
paper, and it is concluded that although 100
percent bagasse paner is of excellent quality,
paper containing 20 percent fiber is preferable.
65-0558
Misra, D. K. Utilizing Kngasse for papermaking
in India Mandvp Mill is significant. Tappi ,
48(7) :8SA-92A, Julv IP'S 5
In India, the shortage of conventional raw
materials for papermaking such as bamboo,
sabai grass, soft wood, rags, and hemp has
caused difficulties in supplving sufficient raw
material. Operation of the first pulp and
paper mill in India to utilize bagasse for
the production of acceptable paper from 100
percent bagasse fiber is described. The
factors involved in the pulping process and
the paper machine operation are discussed
together with the importance of papermaking
to the economy. The collection of depithed
bagasse , the technology developed at the pilot
plant operation, and the significance of the
information obtained in the utilization of
bagasse are covered. Photographs show the
Mandya National Paper Mills, where bagasse is
fed to a denithin? system, haled for storage,
washed, screened, and bleached. There is a
picture of the French-made paper machine with
a 138 in. wire. Data obtained in the
experimental runs on strength of paper, fiber
classification pulp analvsis, and characteristics
of the hagas«e pulp are given. the bagasse
has to be denitbed preferably at the supar
mill anfl enoufh bagasse has to be collected
in the 180 d.pv cruqhinp season to last the
vear. 1Jitb 150 percent bagasse puln, the
speed of the paper machine is limited and the
lenct'1 of the four drinier wire should he
increased to permit adequate water removal.
It is doubtful if a mill based on a 100
percent bagasse pulp is commercially feasible
in the present market
65-0559
Mueller-Rid, W.. and H. Ortner. Stock
preparation from secondary fibers. Part I.
Paper Industry 47(3):50-56, Mar. 1965.
After a short survey of the types of wastepaper
used in Furope, and especially in the Federal
Republic of Germany, their share in the total
supplv of raw material for the paper industry
and tbei'T utilization is briefly mentioned.
The IP." consistency methods of waste paper
stock preparations are described. The
conventional low consistency nethod
requires stock densities of 3 to 5 percent.
whereas the second process requires these low
consistencies only for the primary dissolution
in continuous and discontinuous pulpers. A
combined preparation unit, which means primary
dissolution at low consistency and final
dissolution at high consistency, can also be
employed Four schematic flow sheet
illustrations are given for the various stock
preparation systems. The various pulpers
used in these processes are discussed. After
passing through the pulper the stock is then
passed through a high consistency purifier and
from there it can go with unchanged consistency
to the deflaker. The various high consistency
purifiers and deflakers and their advantages
and disadvantages are described.
65-0560
Mueller-Rid, W., and H. Ortner. Stock
preparation from secondary fibers. Part II.
Paper Industry, 47(4):63-68, Apr. 1965.
Belt thickeners with low power consumption
which are able to increase stock dryness from
3 or 4 percent to 25 to 30 percent or more,
are described and illustrated. The three
machines which have shown satisfactory results
are the belt thickener designed bv Boith, the
double wire thickener by Maschinenfahrik
Andritz, and the ErWePa-thickener. The stock
passes from the belt thickener to one or more
single shaft disintegrators, which are
described, for final deflaking. For deflaking
at high consistencies the Voith single shaft
disintegrator is frequently used. The
disintegrator is not suited for the deflaking
of stock to be regenerated by deinking. The
application and connection of the various
stock preparation machines are explained.
Schematic diagrams are given of: (1) a paper
board stock preparation system producing 180
tons per day of imitation chromo-'ooard, grey
board, and steamed groundwood board; (2) a
stock preparation system combined with a
deinking system; and (3) a paper hoard stock
preparation system in which under! iners are-
made from deinked waste paper. The high
145
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Salvaging
consistency purifying, relining, and deflakinp
machines are also used for pulpers and
fiberizing of large quantities of dry broke
from internal production. In the1 case of
smaller broke quantities, special pulpers
were developed and are described and
illustrated. The reasons for the differences
in the machines needed in the United States
and Europe are discussed.
65-0561
New reclaiming furnace. Waste Trade World,
106(22):7, May 29, 1965.
A new reclaiming furnace, developed for
handling iron-containing aluminum and zinc,
and for charging bulky materials which have
to be run down into ingots, is described.
The charge can also be run into bale-out
furnaces for re-alloying. Melting and
treatment are practically continuous, and as
the molten metal runs from the material being
reclaimed, it is collected in the pouring
end of the furnace for casting purposes. The
furnace is normally fired directly into the
heating chamber by two burners. It is fitted
with recuperating flues positioned in front
by the large charging door, which keep a
uniform temperature throughout the furnace
and retains the heat when the door is onen.
The furnace is fabricated throughout with
heavy steel and lined with the highest grade
refractory to create radiation on the treated
work. It is designed to use minimum fuel
consumption per cwt of metal treated. The
oil can be fed by gravity of the ring method,
or fired by gas. Normal air pressure required
at the burners, supplied from a high-pressure
motorized fan, is 28 in. swg. With normal
flues and ducting fitted above the furnace,
there is an absence of objectionable fumes
and/or smoke.
65-0562
New scrap shearing machine. Waste Trade World,
107(3) :6-7, July 17, 1965.
A new British hydraulically operated
double-sided scrap shearing machine which has
a hold-down capacity of 100 tons and shearing
force of 300 tons is described. This machine
is called the Eldair and is manufactured by
Weldall and Assembly Ltd., Stourbridge. It
has the capacity to handle all classes of
material, inducing 2 in. flat sections,
3-'. in. diameter bars, 3 3/16 in. square sections,
12 bv 5 in. RSJ's, 14 by 4 in. RSC's and any
other material of 10 in. square cross-sectional
area based on 28 to 32 tons tensile MS. The
shear is a compact and self-contained ring
frame type unit, which incorporates a scrap
hold-down. A hydraulic scrap feeder or
vibratory conveyor can be attached to the
frame to form an integral part of the machine.
The hydraulic oil reservoir with a capacity
of 250 gal is carried on the top of two
hydraulic cylinders, the hydraulic pumps
have an operating pressure of 4,480 psi, and
the machine is powered by a 50 hp electric
motor. A feedbox which can be fitted to
the standard machine as an optional is also
described.
65-0563
Ortner, H. The technical state of deinking
by flotation in Europe. Tappi, 48(2):37A-41A,
Feb. 1965.
The consumption of softwood for paper is a
serious drain on the forest reserves in
Germany and Central Europe. In 1963, the
wood saved by deinking and reclaiming amounted
to 12.3 percent of the normal softwood
reserves in the German Federal Republic. It
was found that the costs could be reduced by
equipment now available for deinking. This
review article explains the principle of
flotation of printing ink and gives the
particulars on the power, water, and space
requirements as well as the losses and cost
of a flotation deinking installation. A
flow diagram is given of the equipment used
in deinking and the details of a screw
centrifugal separator which is important in
obtaining compliances with the laws governing
waste water disposal in Europe. Sarikey
diagrams are given showing the water and stock
balances of flotation deinking equipment.
Pictures show a screw centrifuge and a
secondary cell with highly concentrated froth
obtained when air is blown through fibrous
stock suspension containing insoluble calcium
soaps which form sticky surfaces to which the
ink adheres and is carried upward with the
froth. A 50-ton per hr flotation machine is
also shown. Toilet crepe uses 50 to 100
percent of deinked paper, and newsprint
contains 15 to 20 percent. In board mills 100
percent of deinked papers are used in underliners,
blackliners, and topliners. Flotation deinkers
are successful not only in Europe, but in
Argentina, Japan, and South Africa.
65-0564
Paper from cane waste. Waste Trade World,
106(6):8, Feb. 6, 1965.
An announcement is made of the use of bagasse
(sugar cane waste) in a paper mill to be
146
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0561-0568
built at Ishwardi in East Pakistan. Government
permission has been given for its establishment
under the direction of the East Pakistan
Industrial Development Corporation to be
known as the North Bengal Paper Mill. The
mill, which has an estimated cost of Rs
78,010,000, will have an annual production of
16,500 tons of high quality paper.
65-0565
Paper salvage. Public Cleansing, 55(11):610-620,
Nov. 1965.
A joint meeting between British municipal
cleansing officers, and a panel from Thames
Board Mills, which produces 45 percent of the
paperboard and 20 percent of the solid
corrugated cases made in the United Kingdom
is described. T. B. M. consumes 400,000 tons
of waste paper each year. It sponsors
businesses which organize wastepaper and
wasteboard collections from large industrial
users, and aids municipalities, publicizes,
and organizes separate wastepaper collection
from household. The trend is from solid
cardboard to the lighter corrugated board.
Trailers behind packers are convenient separate
wastepaper collection devices. To minimize
the gamble to municipalities who must finance
the institution of a separate wastepaper
collection system, T. B. M. guarantees
acceptance of a minimum tonnage for 3 years
ahead, and a minimum price, relatively stable,
for about 1-.> years.
65-0566
Parthasarathi, M. N. Sources of secondary
zinc and their utilization. Research and
Industry, 10 (11): 329-331 , Nov. 1965.
Although secondary zinc is limited compared
to other metals, a survey was made of the
sources of secondary zinc available in India
in quantity which would not require the
import of specialized equipment for the
recovery of the zinc. Although there would
be collection problems, there is a potential
source in the spent cans from used flashlight
batteries. It appeared that the galvanizing
industry was the most important source of
secondary zinc in India. The residues
available include zinc dross, galvanizer's ash,
flux skimmings, and steam blowings from tube
galvanizing. The dross is an alloy of iron
and zinc containing 96 percent Zn which
settles at the bottom of the zinc bath and is
removed from the galvanizing bath in the form
of lumps which are melted down and cast as
slabs of 'hard zinc' or 'hard spelter' which
is currently used to replace virgin zinc in
brass. At least 10 to 15 percent of the total
zinc used in galvanizing in India is converted
to dross. The zinc may be recovered from the
dross by distillation, which, however, would
require the import of retorts and condensers.
The manufacture of dust from dross, a slight
modification of the distillation technique,
is the best method for utilization of the zinc
dross. Equipment cost of imported material is
only a minor cost compared to the value of
the zinc tonnage recovered. The ash may be
used to manufacture various zinc compounds
and metallic zinc. It was concluded that it
would be in the interests of the country to
encourage the reclamation of Zn from
galvanizing plant residues, either as slabs
or dusts.
65-0567
Portable balers. Waste Trade World, 107(1):19,
July 3, 1965.
The Portabale, a manually operated, mobile
baler which can be taken to the material when
required, is described. The thrust will
depend on the operator, but 1 to 1^; tons is
the average thrust on the bale. The operation
can be carried out by one unskilled operator.
The bales are formed in a detachable truck,
which eliminates handling. Various types
of material such as aluminum, cardboard, paper,
etc., can be baled in an average time of 6
minute with final dimensions 13 in. wide by
28 in. long by 25 to 33 in. high. Price is
fc135. The Electrobale, a power baler with
press-button operations, is also described.
It is capable of handling a wide range of
materials and can be taken to the desired
spot and left to operate automatically in
complete safety. Baling material can be
assembled while a bale is being produced.
Bale size is 30 in. by 30 in. by 14% in.,
and reduction size of bale is possible. Price
is t295.
65-0568
Questions and answers on waste paper for
board. Public Cleansing, 55(4):183-185,
Apr. 1965.
Comments of a cardboard manufacturing company
manager on questions about the market for
wastepaper in Britain are reported. The
demand is much greater than production, and
long-range need will continue to encourage
enlarged marketing and given confidence to
cities considering initiating either salvage
pickerbelts or separate waste paper collection
systems.
147
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Salvaging
650569
Salvage baler. Public Cleansing,
55(5) -.295-299, May 1965.
A new salvage paper baler is described. It
operates pneumatically, loads and cycles
rapidly, and presses about 500 Ib bales.
65-0570
Schroder, F. The research institute for blast
furnace slag and its work. Tonindustrie
Zeitung und Keramische Rundschau, 89(7/8): 146-1 54,
1965.
In steel production more than 100 million
tons of slag are produced worldwide annually.
In the last few years it has been possible to
utilize completely these residues from the
steel production. Through various cooling
processes, the blast furnace slag is converted
into raw material or construction material.
A table lists in detail the manifold treatments
and possibilities of utilization. A research
institute was established in Germany to find
new ways for using the slag and to find new
methods for improving its quality. A detailed
description of the equipment in the laboratories
and various examples of research carried out
by the Institute are given. For instance,
the hydraulic properties and the microstructure
of slag were investigated. (Text-German)
65-0571
Scrap processing plant for Australia. Waste
Trade World, 107(2):13, July 10, 1965.
M and T Chemical have ordered a Scrapmaster
TGS101 from Sheppards of Bridgend, England,
for their new Australian works. The TGS101
is a bigger version of the popular TGS57.
It has a charging chamber 40 in. wide, 36 in.
deep and 100 in. long. Bale sizes are 12 in.
by 12 in. by variable, 14 in. by 14 in. or 16
in. by 16 in. variable length. Output averages
100 bales an hour. The TGS101 has the unique
Scrapmaster method of operation, which subjects
scrap in the charging box to three separate
and independent compressions. This produces
bales of dense construction, a typical bale
weighing 22 Ib per in. of length.
65-0572
Sintered fly ash goes to market. Electrical
World, 163(26) :94-95, 142, June 28, 1965.
Consolidated Edison Co. is now commercially
converting fly ash into lightweight aggregate
for use in concrete products at a new S3
million sintering plant with a capacity of
1,000 tons per day. This sintered product is
competitive in price and produces concrete of
the same strength as ordinary aggregate, but
weighs one-third less per cu ft. A diagram
portrays the sintering process from the
collection of the fly ash on the precipitators
to the final load-out stage. The fly ash is
pelletized without binder admixtures and
fused at 2,300 C to form a hard porous
material. The fly ash which is collected
at the precipitators of the five Astoria
generating station boilers is transported
pneumatically from the collectors to the
sintering plant through steel pipes. Studies
indicate it would not be economical to
transport the fly ash collected at other
stations by truck to Astoria. Structural
grade sintered fly ash is delivered to the
ready-mix concrete plants in the nominal sizes
of **- in. to No. 4 as called for in the American
Society of Testing Materials specification
C330. Ninety-five percent of the finished
product consists of unbroken pellets.
65-0573
Smith, W. H. Kraft pulping from sawdust and
shavings in a continuous digester. Paper
Industry, 47(8):45-46, Aug. 1965.
A continuous digester for the production of
kraft pulp made from sawdust and shavings is
described. The sawdust and shavings delivered
to the mill are screened to remove oversize
material and then run through a Verti-Flex to
even the hulk density of the material and
facilitate feeding into the digester. A
moisture detector is included among the
preparatory steps and reads out a correct
percentage B.D. of the material, which
allows further control of the residuals to
the digester to maintain the B.D. tonnage at
50 percent B.D. weight of the material. This
feature is very important since control of
wood rate to a given percentage B.D. is
necessary for the control of pulp quality.
The continuous digester is powered by a 10 hp
variable-speed drive unit which gives a
retention time of 20 to 40 minute. White and
black liquor are added to the digester to
maintain desired kappa number and total
volume and level. Steam is added to the top
of the digester to maintain an operating
pressure of 145 psi and a cooking temperature
of 365 F. Steam consumption averages 4.0 M
Ib per pulp ton. Stock is discharged through
an outlet valve and pulp is blown into a
cone-bottomed blow tank, where it is diluted
to a consistency of 3.5 percent and then
pumped to another blow tank and nixed with
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0569-0578
pulp made from chips in stationary digesters.
The pulp mixture is washed and screened over
vacuum washers. Values are given for tests
on the pulp made from sawdust and shavings.
Present developments to improve and expand the
residual cooking and handling system are
outlined.
65-0574
Stevens, R. P. New machines speed corrugated
collection and disposal. Refuse Removal
Journal, 8(10):25, Oct. 1965.
There are three major sources of paper stock
available. The first is the direct producer
such as box shops and others that bale their
own material. This source produces the best
quality paper stock. The second source is
that stock baled at various landfill sites.
This is usually free from contaminants if a
moderate amount of supervision is maintained
over the salvage operators. The largest
suppliers, refuse removal companies, are dealt
with in greatest detail in this article.
Salvaging is made more difficult by various
contaminants present in refuse, such as
wax- and foil-coated stock and plastic bags.
The most commonly used method for handling
old corrugated cartons is the transfer body.
This is an expensive method, however, and
the installation of hoggers and shredders and
new more integrated methods promises a less
expensive and more efficient method of
salvage.
650575
Stirrup. F. L. Salvage and utilization. In
Public cleansing; refuse disposal. Oxford, The
Institute of Public Cleansing, 1965. p.119-136.
Salvage is material sorted from refuse and
prepared for sale as a raw material which can
be incorporated in the manufacture of commodities.
Utilization is the treatment of conversion of
parts of a mass of refuse to make it usable in
industry, agriculture of domestic life. Waste
paper must be free from dirt, collected separately
and sorted into grades. A conveyor of woven
wire mesh allows dust and small contraries to
pass through. The paper enters either the
continuous or swivel box baler. It then enters
single or twin ram fixed box press and is
stored in twin ram movable boxes. Tins and small
ferrous metals are removed by magnet and
baled; larger ferrous metals are picked by
hand. The primary non-ferrous metals utilized
are copper, brass, aluminum, and lead. Textiles
are sorted into woolens, mixed rages, sacking
and bagsin?, carpets, and string. Glass cullet
is sorted into white and colored. Bones are
used for glue, fat, and bone meal. Rubber
basically is not salvaged. Food wastes are
to be heated if used as a feeding stuff.
By-products from animal wastes: blood,
condemned meat and fish, bones, carcasses,
and offal can be used for fats, grease, and
fertilizers. Moisture content should be less
than 10 percent to prevent mold. Fuel can be
made from refuse briquettes, but it will
disintegrate if exposed to moisture.
65-0576
Taconite reacted with steel scrap can become
feed to a blast furnace. Chemical Engineering,
72(3) :22, Feb. 1 , 1965.
The Bureau of Mines of the Interior Department
has developed a process which converts
nonmagnetic taconite into magnetite by
reaction with scrap steel, which also changes
into magnetite, a product widely used as raw
material for blast furnaces.
65-0577
Thorman. Conference in Weimar on the
utilization of blast furnace slag.
Tonindustrie Zeitung und Keramische Rundschau,
89(13-14) :308-309, 1965.
At the University for Architecture and
Construction in Weimar, Germany, a meeting
was held in April 1965. Several papers were
presented, mainly on the utilization of blast
furnace slag. The addition of slag to concrete
was suggested. The sintering of slag was
discussed as well as the influence of
manganese oxide and aluminum oxide on the
water affinity of slag, the utilization of
slag in construction, etc. Eleven articles
were presented. The contents of each is
briefly mentioned. (Text-German)
65-0578
Trailers hooked to packers speed waste paper
collection. Refuse Removal Journal, 8(11):28,
Nov. 1965.
An English sanitation department initiated
use of small, two-wheeled trailers for waste
paper behind regular packers. Reported
advantages include better service, economizing
landfill space, extending life of equipment,
and additional bonuses to workers from the
sale of 3h tons of paper collected by each
team weekly.
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65-0579
Trim removal plant. Research and Industry,
10(2):48, Feb. 1965.
A new trim removal plant, the 'Perflo Duct'
which collects and removes all types of paper,
cardboard, synthetic film and foil separately,
is described, The device, developed by
Musgrave & Co. Ltd., Belfast, United Kingdom,
disposes of three different types of wastes
without mixing them. The arrangement reduces
capital and operating costs since the one
device replaces three waste disposal machines.
A photograph shows the trim removal machine
which consists of a duct with three channels to
transport the waste pneumatically from the
machine to a discharge point. A machine in
the production line is connected to any
channel and the other two channels are
blanked off at that machine. If the next
machine has a different by-product it is
connected to a different channel to keep the
by-products separate. Perforated walls
between each channel ensure free flow of air
and adequate transport velocity throughout the
system independent of the sequence of machine
operation. A fan at the remote end of the
duct sucks the by-products to the discharge
point. The costs of disposal of mixed wastes
is minimized by sorting the various types of
trim at the point of origin and removing them
unmixed, pneumatically to the discharge point.
65-0580
U.S. srive for scrap pay-off. Waste Trade
World, 106(15) :10, Apr. 10, 1965.
The conservation and reclamation of scrap are
necessary to preserve resources and to protect
the economy by providing the necessary raw
materials for the manufacture of essential
military and civilian items. With
technological advances in military equipment,
much of the material rapidly becomes obsolete
and is ready for the scrap heap together with
worn out material. The Defense Logistics
Services Center at Battle Creek, Michigan,
which has as its main objective to get the
highest return possible for obsolete and scrap
material, has trained over 1,200 from all the
military services in the identification and
segregation of scrap metal in schools and in
clinics conducted throughout the country. The
Defense Department has long recognized that
identification and segregation pays, although
the identification of modern metals and alloys
is difficult , Every effort is being made to
improve, modernize, and develop new techniques
for tbe identification, segregation, and
merchandising of scrap metals. In 1964, the
Departnent of Defense realized $23 million
from government scrap yards including 436,612
tons of ferrous and 90,878 tons of non-ferrous
scrap. The sales of precious, ferrous and
non-ferrous scrap metal accounted for more
than 28 percent of the sales of all Department
of Defense surplus material. There has been
a 30 percent increase in non-ferrous proceeds
during a three-year period ending June 30,
1964. A paper given by John W. McVicar,
Defense Surplus Sales Officer Chief in March
1964 to "he National Association of Secondary
Material Industries Convention is summarized.
65-0581
Using computers to cut costs in making alloys
from scrap. Waste Trade World, 106(16):10-12 ,
Apr. 17, 1965.
It is general practice to use rough 'rule of
thumb' calculations coupled with wide
experience in the production of alloys from
scrap. While this method gives excellent
results, its weakness is that it is dependent
on human judgement which varies from day to
day and that calculations, in order to be
done swiftly, must contain small inaccuracies
and estimates which may cancel each other out,
but may also result in errors of sizeable
proportions. To make accurate assessments
there is a general technique, known as the
linear programming algorithm, which may be
applied to such a problem as the blending of
metals to make an alloy. Experiments using
this tecinique showed that savings in the region
of 10 percent in the cost of producing alloys
were frequently possible. Computers which
can be bought or rented can perform these
calculations quickly and accurately for
between fc10 and E100, depending on the
complexity of the problem.
65-0582
Utilizing waste oil. Waste Trade World,
107(13):S-7, Sept. 25, 1965.
Activities and exhibits at the Plant Exhibition
and Demonst'ration, organized recently in
Liverpool by the North-West Branch of the
Contractors' Mechanical Plant Engineers, are
reported. There was a lot of interest in
special tires, particularly in partly used
and large-size earthmovers. A waste oil
burning heater which has been developed over
a number of years to handle the twin problems
of waste oil disposal and provision of heat
in the workshop is described. All kinds of
waste oil are burned cleanly in the Anderton
without smoke or fumes, and it can be used as
a space heater or for central heating and hot
150
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0579-0586
water supply. Output is 80,000 Btu's on all
types of fuel. Other exhibits include the
Atlas 3001 hydraulic lorry loader with new
designing of boom and jib, the Avenger 10-ton
lorry-mounted crane with a job unloader of
simple construction, mobile cranes of 6, 10,
and 15-ton capacity, and different types of
grabs including a Bernard tentacle-type
grab — all particularly useful in scrap handling.
650583
Utilizing forest waste. Waste Trade World,
106(11) :7, Mar. 13, 1965.
A small state company in Hungary employs 1,400
permanent and 25,000 seasonal workers to
scavenge forests for mushrooms, wild fruits,
cones, and bits of wood previously considered
without value. The timber scrap is purchased
by small workshops to make into tool handles
and kitchen spoons. Over 200 tons of birch
twigs are exported to the West each year.
The annual turnover of this forest 'scrap' is
t2 million.
65-0584
Weiss, A. J. Guitar maker burns wood waste
to heat plant. Heating, Piping and Air
Conditioning, 37(7):91-95, July 1965.
The Kay Musical Instrument Co. , which
manufactures stringed musical instruments by
a combination of machine and hand operations,
has built into its new plant equipment which
facilitates the burning of wood waste to heat
the plant. Sawdust and wood are produced at
rates up to 900 Ib per hr and on a two-shift
basis require two 165 hp boilers with
wood-burning equipment. Woodworking machines
are provided with hoods for collection of
sawdust, and twin exhaust systems convey
sawdust and shavings to a cyclone dust separator
located above the boiler room. A rotary
grinding mill reduces scrap to a size suitable
for suspension burning. Large chunks of
scrap material were originally fed into a
wood grinder or hog, and discharged into the
storage bin from a small separator. Problems
in packing which arose from this method were
solved by installation of a large cyclone
which provided a more uniform material texture.
The exhaust requirements of wood dust
collection make it necessary to supply 100,000
cfm of tempered makeup air, which imposes a
significant load on the boilers. Therefore,
boilers with a total capacity of 330 hp are
needed. Wood scrap it, augered from the
storage bin and dumped into the intake of a
pneumatic conveying system, which delivers a
mixture of wood and air to a boiler's firebox.
Estimates on the basis of two-shift operation
indicate the cost of natural gas for heating
the plant wr.uld be $20,000 per year, while
with the above procedure the savings in fuel
costs will approximate $17,000.
65-0585
Wenzl, H. Developments in recovery of sulfite
cooking chemicals. Paper Trade Journal,
149(24):51-59, June 14, 1965.
The various recovery methods for sulfite
cooking chemicals with magnesium, sodium,
ard ammonium bases, as well as recovery systems
for sulphur, are reviewed with reference to
the literature. The process steps involved
in the recovery of sulfite chemicals include:
(1) evaporation or concentration of the spent
liquor with liberated sulfur dioxide gas
returning to liquor preparations; (2) combustion
of concentrated liquor with liberated sulfur
dioxide returning to liquor preparation; and
(3) chemical conversion of the basic substances
present in the smelt. Sodium base recovery
methods involve two types of processes; the
liberation of hydrogen sulfide from the ash
containing sodium carbonate and sodium sulfide,
and the direct oxidation of sulfide to
sulfite. Those described in detail with
accompanying flow diagrams art- the Mead process
based on sodium sulfite semi-chemical cooking;
the Western Precipitation process based on
separation by crystallization of the sodium
carbonate and sodium sulfide from the smelt;
the Sivola process based on two-stage cooking;
and the Stora Kopparberg process which
recovers elemental sulfur by dissolving the
smelt from the recovery boiler. Other processes
which require less evaporation or direct
treatment of the spent liquor are described,
including the AST process (atomized suspension
technique) based on pyrolysis of the solids
in the spent liquor and their conversion into
gases, and the SCA-Billerud process based
on the recovery of cations from the spent
liquor by ion exchange. Ion exchange recovery
methods. which require no previous
concentration of the liquor and which use
cation exchangers of the sulfonic acid type,
are discussed, as well as electrodialysis,
ammonium and magnesium base recovery, and cross
recovery systems.
SANITARY LANDFILL
65-0586
Attig. G. K., and J. Clay. County in
Oregon opens landfill to all citizens.
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Sanitary Landfill
Refuse Removal Journal, 8(4):16-17,
28, Apr. 1965.
Oregon's Lane County operates a sanitary
landfill which is available to the public.
Heavier compaction equipment has doubled
the lifetime of the fill, which will be
developed into a county Park when
completed.
landfill techniques eliminate nuisance and
public health hazards, they will continue
to be more commonly used. Questions
concerning costs, the water table, seasonal
operations, the degrading of landfill sites,
weighing, the mechanics of compaction,
resident setback, and others were answered
after the formal paper.
65-0587
Bishop, W. D., R. C. Carter, and H. F.
Ludwig. Gas movement in landfilled
rubbish. Public Works, 96(11):64-68,
Nov. 1965.
A test refuse fill was built in Southern
California to determine the quantities of
decomposition gases passing into the
soil. Carbon dioxide was the only gas
found in significant quantities in the
adjacent soil. The reason for the
experiment was to determine possible damage
to the ground water supply from a sanitary
landfill.
65-0588
Black, R. Sanitary landfills. In
Proceedings; Technical and Planning
Aspects of Solid Wastes, Columbus, Sept.
1965. Ohio Department of Healti, p.G-1
to G-26.
Sanitary landfill is defined, emphasizing
that the refuse must be covered with a
layer of earth at the end of each day
or at more frequent intervals if necessary.
Four methods of disposing of refuse on
land are: open dumping, controlled burned
dumping, refuse filling, and sanitary
landfilling. Their respective costs are
given and the methods are compared.
Successful sanitary landfill operations
have competent and continuing engineering
planning and control. Research in the
field is noted. The operation of three
sanitary landfills in the Los Angeles
County area are specifically examined.
One of the important advantages of the
sanitary landfill is that variations in
the character or the quantity of the
refuse received have little effect on
normal operations. Since cities must
dispose of large portions of their refuse
on land, whether incineration, composting,
or some other volume reduction method is
also used, some type of land disposal
will continue to be widely practiced in
the United States. Since present sanitary
65-0589
Booth, F,. J. Buried 25 years and still
legible. American City, 80(7):26, July
1965.
The opening of a 25 year old landfill
has revealed papers and books that are
still legible and auto motors still in
good shape, indicating the slow decomposal
rate in landfills, particularly in dry
65-0590
Controlled tipping must continue. Surveyor
and Municipal Engineer, 125(3809) :49 ,
June 5, 1965.
The need for controlled tipping in spite
of the increasing trend towards the
pretreatment of refuse by incineration,
pulverization, and composting was
discussed by S, K. Sheldon in a paper
given to the Institute of Public Cleansing
Conference at Scarborough this week. It
would be uneconomic and physically impossible
to change the form of disposal now being
used by most authorities in the near
future. The recruitment of suitable tipmen
is a problem, because of the nature of the
work. The men should be given a sense of
partnership in a worthwhile project. They
should be outfitted with first-class
protective clothing, a warm, clean,
dry cabin with simple washing facilities
and the best possible amenities. The
changing nature of refuse, with the
increase in paper and cans has created
difficulties at the dumps by creating
voids which cause uneven sinkage, difficult)
in covering, and nuisance from blown
refuse. Consolidation of the surface near
the tip face to reduce the voids before
covering can be obtained by bulldozers,
loading shovels, or the use of the refuse
vehicles to run in the surface will help
with the problem, although a greater amount
of covering will be needed than formerly.
The surface of the tipping bay becomes
rigid and corrugated from the uneven
settling and this hazard to the trucks
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0587-0594
can be controlled by backblading and
filling of the depressions. Chicken wire
at the tip face is used to control light
wind-blown refuse. Controlled tipping
must continue and the necessary steps
should be taken to lessen the present
problems.
65-0591
Denver's new fill to last 40 years. Refuse
Removal Journal, 8(3):14, Mar. 1965.
Denver, Colorado is spending a total of
$370,000 for the expansion and
modernization of its refuse handling
facilities. The city is building a
$295,000 equipment service yard and
trash transfer station on a recently
purchased 26-acre site. Anothe- $75,000
is allocated for landfill and earth-moving
equipment that will be used at its new
dump site on the old Lowry Air Force
Base bombing range. The city has title to
2,680 acres of prairie land that was
once part of the Lowry bombing range. This
virgin area is sufficient to take care
of Denver's needs for the next 40 years.
The new transfer station will be used as
a point where rubbish compaction trucks
on regular neighborhood pick up routes
can empty their loads into larger
carriers for the long haul out to the
bombing range landfill. It will also be
a materials storage yard. When the two
sites are in operation it will permit the
city to discontinue its trash burning
activities at a location east of town.
Sept. 1965. Ohio Department of Health.
p.F-1 to F-10.
Although open dumps are archaic, they are
the most prevalent method of solid waste
disposal. The operation of an open dump
requires construction equipment for
'dozing' down the dumped refuse which are
financed through revenue all too frequently
obtained through other departmental funds.
An open dump can cause air and water
pollution. Refuse contains mineral and
organic substances which can seriously
pollute underground water supplies. Data
is furnished showing the necessity for
better refuse disposal methods through the
control of disease vectors. The
host-parasite and host-vector relationship
is a complex interplay of the factors
of reservoir, parasite, vector, and
host which result in disease or immunity.
Although it is difficult to eliminate
any one of these factors, the partial
reduction of any two reduces the potential
of vector-borne diseases. The reduction
of food and harborage through the
elimination of the open durrn will reduce
the factors representing vectors, reservoirs,
and associated parasites. The particular
vectors and the diseases they transmit
are listed. The problems involved in the
conversion of an open dump to a sanitary
landfill are considered, A properly
operated sanitary landfill eliminates
burning and decreases pollution. The
employment of a pest control officer to
eliminate the rodent-vector before the
closure of an open dump is suggested.
There must be total planning.
65-0592
Early bird gets a 60-acre bonus.
American City, 80(11):44, Nov. 1965.
The City of Raleigh, North Carolina,
switched to sanitary landfill in 1939.
Because of this decision, Raleigh now
has 60 acres of reclaimed land adapted
to park and commercial use. The
Division of Sanitation employs an
International 175 loader and a Hough
H50 to work current landfill sites. The
ramp-trench method disposes of more than
1,500 cu yd of refuse per day.
65-0593
Eldredge, R. W. Open dumps. In
Proceedings; Technical and Planning
Aspects of Solid Wastes, Columbus,
65-0594
Engineering-Science, Inc. In-situ
investigation of movement of ga- es
produced from decomposing refuse.
Sacramento, California State Water
Quality Control Board, 1965. 211 p.
This study was made to determine the
amount of ground water pollution resulting
from movement of gases within the soil.
The test site used for thi;; study is
located in a three-quarter acre pocket
situated in the floor of a gravel
excavation directly east of the Sante
Fe Flood Control Dam. Walls of the pit
are approximately 100 ft in height with
walls of the pocket 25 ft in height on
three sides. Selected refuse was
domestic and residential with no
industrial-, commercial-, or
demolition-type material included.
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Sanitary Landfill
Forty-two gas sampling probes and thirteen
combination temperature-moisture detection
units were installed. Thirteen gas
sampliig wells were drilled outside the fill
area. A fourteenth well was drilled through
the center of the fill itself. At least
monthly sampling analysis of probes
within and outside refuse fill were
made for determining gas production and
movement during the early and later stages
including determinations of water, methane,
hydrogen, carbon dioxide, hydrogen sulfide,
or oxygen and nitrogen. Porosity of soil
was determined and monitoring of
temperature, relative humiditv, pressure,
and rate of decomposition of the fill.
Results showed carbon dioxide being the
only apparent decomposition gas passing
into the soil in significant quantity.
Calculations show that by far the greater
amount of carbon dioxide leaving the
refuse goes into the atmosphere. Predictions
are made for rate of carbon dioxide
movement in future years. Present studies
are being made for control of gas
movement from refuse landfill.
65-0595
Goodrow, T. E. Sanitary landfill becomes
major league training field. Public
Works, 96(8):124-126, Aug. 1965.
The construction of a baseball field
out of a sanitary landfill in St.
Petersburg, Florida, for the St. Louis
Cardinals' farm teams is described.
65-0596
Hachett, J., B. Black, and R. Smith.
Sanitary landfills. In Proceedings;
Technical and Planning Aspects of Solid
Wastes, Columbus, Sept. 1965. Ohio
Department of Health. p.H-1 to H-25.
Landfill results in a large variety of
waste products with many chemical and
biological constituents. These can be
classified into: domestic refuse,
industrial waste, used construction
material, and incinerator ashes. The
physical environment of the landfill site
is affected by: the rates of decomposition
of the fill, the production of contaminants,
the retention or spread of these products
which are determined by the meteorological,
geological, and hydrological conditions
of the site. Meteorological factors
include precipitation, evapotranspiration,
and soil moisture. Berkeley, California
is analyzed for these factors. Geologic
factors include permeability and the rock
categories of un-consolidated material,
consolidated sediments, chemical
precipitates, and igneous and metamorphic
materials. Various species of rats
are found at dump sites. Other wildlife
problems cited are the problem of dogs
and cats attacking people and spreading
rabies, and sea gulls and other bird
problems. All the wildlife problems of any
type can be solved by removing the
garbage (the food source). Questions
about the control of snakes around dumps,
the use of dumps by game birds, and
chemical applications were answered.
Other questions were about the data
available through the state or the U.S.
Geological Survey, and possible chemical
pollution of wells in a sand and gravel
strata.
65-0597
How to use your completed landfills.
American City, 80(8):91-94, Aug. 1965.
Results of a survey conducted by The
American City on municipal use of completed
sanitary landfills are reported. Gas
production and ground settlement were
the two main problems. Houses, buildings,
roads, and sewer and water lines all
suffered from settlement, and five
dangers developed in basements of
buildings built on or near completed
landfills. Pilings through the landfill
offered good foundational support;
however, excavating in old landfills was
an odoriferous process. Minimum housing
requirements are suggested. About 90
percent of the settlement takes place in
the first 5 years after a lardfill
is completed. Parks, golf courses,
playgrounds, water pollution control
plants, parking areas and supply yards
were all successfully operated on completed
fills, although methane gas problems
occasionally had to be solved. The
success and failure of a variety
of municipal landfill use projects are
recorded.
65-0598
Hueppelsheuser, L. D. For putrescibles
only. American City, 80(1):18, Jan. 1965.
Flagstaff, Arizona, has changed from an
open dump to a trench-type, 29-acre
sanitary landfill, which only accepts
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0595-0605
putrescibles because of the scarcity
of sites. A northwest dragline with a
one-cu-yd bucket excavates the trench.
65-0599
Kandra, G. A. Tire failure no longer a
problem. American City, 80(3):104-105,
Mar. 1965.
the incoming refuse for better compaction
was abandoned because mud and debris
repeatedly clogged the inlet strainer,
the swamp water had a foul odor, excess
water muddied the truck route, and the
long pipeline interfered with the
operation of the landfill. An Allis-Chalmers
HD 21 dozer is used for compacting the
refuse, and spreading the cover material
which is obtainr^1 from a nearby quarry.
Bativia, New York, has switched from a
track-type tractor to a rubber-tired
loader for its sanitary landfill operation.
The loader provided a higher degree of
maneuverability while compacting and
backfilling, reduced shuttle time between
the borrow pit and the working face of
the fill and thereby eliminated a dump
truck, compacted the refuse more thoroughly,
and was more economical.
650602
Landfill replaces open dump. Refuse
Removal Journal, 8(3):24, Mar. 1965.
Wetumpka, Alabama, replaced an open
dump, which was a constant health hazard
and eye sore, with a sanitary landfill.
65-0600
Koch, A. S. Sanitary landfill lives up
to the county's expectations. Public
Works, 96 (7): 70-71, July 1965.
In 1959 after extensive study, Orange
County, California, produced a 'Master
Plan of Refuse Disposal' which was to
provide guidelines for solving its shortage
of disposal sites for at least 20 years.
So far the plan has been successful
and economical. It currently calls for
the employment of three canyon-bottom
landfill sites and three transfer
stations.
65-0601
Kunimoto, Y. For better breathing: a
landfill. American City, 80(10):62,
Oct. 1965.
Landfill operations conducted by the City
and County of Honolulu, Hawaii, are
described. The landfill replaces an
odiferous, smoking, open dump located
in an area subject to atmospheric
inversions. The numerous complaints
received from residents, particularly
bronchitis and asthma sufferers, stopped
abruptly as soon as conversion took
place. The landfill operates seven
days per week. Residents deposit
their trash without charge, but businesses
must pay $0.75 for the first cu yd and
$0.50 for each additional yd per truck
load. The landfill disposes of about
5,600 ton per month. Wetting down
65-0603
Langer, W. Measures and facilities for
the protection of potable water reservoir
areas. Wasser und Abwasser, 106(8):
207-211, Feb. 1965.
To protect the drinking water in valleys
dammed for water supply purposes, no
waste whatsoever may be deposited in
reservoir areas without previously testing
the water permeability of the ground. It
is recommended that sanitary landfills
be established outside the protection
area. Very often waste is dumped into
ditches and behind bushes so that it
cannot be seen but it can contaminate the
drinking water. No traffic should be
allowed to go through such areas because
traffic brings a lot of waste along with
it. (Text-German)
650604
Los Angeles warned about shrinking
disposal areas. Refuse Removal Journal,
8(9):29, Sept. 1965.
In a report on the status of refuse
disposal facilities in Los Angeles
County, John A. Lambie, County Engineer,
said that at least six more landfill
sites should be acquired soon to keep
abreast with the growing population.
65-0605
Milwaukee facing shake-up due to lack
of disposal sites. Refuse Removal
Journal, 8(2):24, Feb. 1965.
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Sanitary Landfill
Milwaukee, Wisconsin, is considering
a proposal to increase incineration if
they cannot find a suitable landfill site.
The City also might combine the Garbage
Collection Bureau and the Bureau of Stre
Sanitation into a Bureau of Sanitation fot
economic savings.
65-0606
Obtain fill areas by tax foreclosure.
Refuse Removal Journal, 8(2):35, Feb.
1965.
Thirty-nine acres of undeveloped railroad
property have been obtained through a
tax foreclosure by the City of Newark,
New Jersey, and will be used as refuse
dumping grounds. The new acreage is
expected to be useful for 5 to 6 ysars,
and will save $30,000 in disposal costs
for 1965. Newark now dumps most of its
refuse in nearby Kearny, but the pact
expires in 1969 and a renewal is not
expected. Since New Jersey health laws
require, for every 4 ft of refuse dumped,
a 12 to 18-in. covering layer must be
spread, Newark presently spends about
$50,000 a year for landfill cover
material. Some of the new land, when
completely filled, will be suitable
for redevelopment. If all refuse
dumping had to be done at Kearny, it
would have meant $250,000 in increased
costs.
65-0607
Parkhurst, J. D. Sanitary landfill
operations in Los Angeles. Sanitary
landfill operations in Los Angeles.
Public Works, 96(11):54, 56, 1965.
Since 1955 design and manufacture of
earth moving machinery have been
improved; this machinery provides the
primary tools for sanitary landfilling.
Refuse in Los Angeles is pushed up
a ramp for compaction on about a 20
percent slope by crawler tractors of
approximately 50,000 Ib gross weight
equipped with U-blades. As tonnage
increases, self-propelled, rubber
tired scrapers are used to cover the
refuse with earth. These are of
the twin-engine type, witb all-wheel
drive, most being able to load themselves
without aid from a tractor. The smaller
sites have 14-cu yd machines, and thp
larger sites 24 cu yd units. Water wagons
are also a necessary equipnent used
extensively for dust control on roadways
and at the dumping area. The latest
machines have a 6,000-gal capacity,
with custom-made tankers built around the
tractor of a single-engine scraper. They
have a special low-profile design to
provide operator visibility, and are equipped
with a special monitor aimed with air-
operated cylinders which can spray up to
100 ft. The per ton operating costs at
District landfills have remained stable
and even decreased slightly, while
general construction costs rose about 30
percent.
65-0608
Qasim, S. R. Literature review. In Chemical
characteristics of seepage water from
simulated landfills. Morgantown, West
Virginia University, 1965. p.3-20.
A total of 55 papers and reports are covered,
all pertinent to the research carried out.
Topics reviewed are: breeding of pest
in refuse and the possible spread of
disease; water and air pollution from
waste; sanitary landfill as an effective
means of disposal; and methods of landfill--
their degree of compaction and amount of
settling. The information of the amounts
of refuse produced and its physical
composition from a number of cities is
combined into a table. The chemical
composition of mixed refuse is dealt
with, and a table combines the information
from several sources. Data on heat
generated in compacted landfill refuse
from several sources is discussed. The
chemical analysis of material leached
from landfills, the effect of degree of
deconposition on the materials leached
out and their possible contribution to
ground water pollution are covered next.
Studies on the changes in bacterial
population with the age of the fill and
the ability of the soil to filter out
bacteria from seepage is also discussed.
Data showing the similarity of leaching
to chromatographic action are included.
65-0609
Qasim, S. R. Summary. In Chemical
characteristics of seepage water from
simulated landfills. Morgantown,
West Virginia University, 1965. p.104-106.
Temperature rise could not be used to
reflect the progress of microbial
activitv because of excessive heat loss
156
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Ob06-0612
through the walls of the cylinders.
The maximum settlement rate occurs in
the first two weeks. Percolation of
water through the refuse beds is delayed
due to high moisture retaining capacity of
the refuse (a.62 in. of water per ft of
bed depth). The leach samples were
rich in both organic and inorganic
components, the deeper the fill the higher
the concentration but, on a per foot of fill
depth basis, less was extracted from the
deeper fills. The percent reduction of
leached materials during the test period
was greatest for the shallower fills. For
the leaching of chloride there was good
agreement between experimental and
theoretical results based on Thomas and
Hiester's column ion-exchange and adsorption
process. The pH of the end of the
experiment the total bacterial population
was down from 92 to 97 percent and the
coliform group by from 97 to 99 percent.
The leach samples were well buffered at
all times (a high acid and base
neutralizing capacity) due to the formation
of weak acids from decomposition of
organic matter. An assessment of
pollution based on the extracted material
from the fills showed that for an
equal amount of influent shallower fills
had a greater extraction rate per
acre-foot and were therefore a greater
pollution hazard. Volatile contents of
the refuse decreased with time and
leaching. The nitrogen deficient portions
of the refuse showed an increase in
nitrogen as leaching was continued. The
C:N ratio decreased with time.
65-0610
Qasim, S. R. Conclusions and recommendations.
In Chemical characteristics of seepage
water from simulated landfills. Morgantown,
West Virginia University, 1965. p.107-108.
Refuse fills are capable of seriously
polluting underground water reservoirs
through percolation and movement of
carbon dioxide through the aquifiers causing
an appreciable increase in hardness, iron,
solids and different forms of nitrogen and
sulfur. Although the chemical quality
of seepage water and the magnitude and
rate of extraction of material by it are
determined, the dispersion phenomena during
movement of pollutants needs further
investigation. The permeability of the
strata will decrease considerably during
movement of pollutants from the fills,
but whether an impervious coating or layer
will form and break the moisture profile is
not known. Since they affect the concentration
of underground pollutants, data on the
velocity, and direction of ground water
movement and the depth of water bearing
strata under prospective landfill sites
will delineate the magnitude of the danger
of pollution. Large volumes of carbon
dioxide produced during the aerobic and
anaerobic decomposition of refuse, if moved
through the aquif:>r, will dissolve various
minerals and degrade ground water quality.
Methods to limit the gas penetration into
the aquifier are desirable and should be
investigated. Preliminary work with jar
tests showed that various materials are
released from refuse at different
rates at various materials are released
from refuse at different rates at
various incubation temperatures. Information
on the optimum mesophilic and thermophilic
temperatures for the release of various
materials from the refuse will be of
great importance.
65 0611
Qasim, S. R, Appendix A. Methods and
apparatus used in chemical and bacteriological
analyses. In Chemical characteristics
of seepage water from simulated landfills.
Morgantown, West Virginia University,
1965. p.109-113.
Most of the methods used have been taken
from the Standard Methods for the Examination
of Water and Waste Water, 11th edition,
1960. Some of the modified methods have
also been adopted for convenience. The
information is presented in table form,
the headings of which are: tests (the
parameter), methods and special reference
other than (Standard Methods), apparr^us,
and remarks (special conditions or
changes) .
65-0612
Qasim, S. R. Appendix B. Simulated
landfill, temperature records, analyses of
leach samples and refuse. In Chemical
characteristics of seepage water from
simulated landfills. Morgantown, West
Virginia University, 1965. p.114-138.
All information is tabulated. For
temperature: the date and time of
and the air temperature at that time are
given together with the temperature of the
fill at various heights above the fill
floor and the ag<- of the fill at the
time of measurement. For each leach sample
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Sanitary Landfill
taken, the results of the analysis for
each of the following parameters are
listed: total solids (mg per liter,
volatile solids (mg per liter) , alkalinity
(as mg per liter CaC03, end point pH 3.8),
acidity (as mg per liter CaC03, end point
pH 7.2), hardness ((EDTA) as mg per liter),
total iron (mg per liter), chloride
(mg per liter) , sulfate (mg per liter),
total phosphate (mg per liter) , tannin
and lignin (mg per liter), BOD. (mg per
liter), ammonia nitrogen (mg per liter,
organic nitrogen (mg per liter) , total
nitrogen (mg per liter) , pH, MPN
(presumptive test) , Standard plate count
(20 C, 48 hr) , spot check fluoride
(mg per liter) , spot check aluminum
(mg per liter) , spot check silica as
S102 (mg per liter), spot check boion
(mg per liter) , spot check detergents
(total apparent ABS (mg per liter)).
Another table gives the cumulative values
for each cylinder for each of the taken
gives the cumulative values for each
cylinder for each of the parameters listed
above through total nitrogen. For each
refuse sample taken from the simulated fills
the following are reported: moisture content
percent wet weight, volatile solids
percent dry weight, ash content percent
dry weight, total nitrogen percent dry
weight, approximate carbon content
percent dry weight, and approximate
C:N ratio.
65-0613
Quarries become landfill in Texas. Refuse
Removal Journal, 8(10):10-11, Oct. 1965.
San Antonio, Texas, has turned unhealthy
and abandoned quarries into sanitary
landfill sites. Some of the completed
landfills have been converted into public
recreation areas and parking lots. The
city's collection and disposal system
is highly efficient and the cheapest of
the major U.S. municipalities.
65-0614
Sanitary fill supermechanized. American
City, 80(12):20, Dec. 1965.
A new machine manufactured by the D and
J Press Co. promises the ultimate in
sanitary landfills. It compresses the
refuse to less than 15 percent of its
original volume in a compactor truck. It
extrudes this tightly packed package into
a trench that its excavating section has
just dug, and covers it without the aid
of other equipment. Two men operate the Bip
Squeeze refuse-disposal machine. The man
in the forward cab controls the trenching,
backfilling and earth-compacting operation,
while the operator in the rear cab loads
the hopper and controls all refuse-compacting
operations. Two 450-hp V-12 diesel engines
supply all power. The refuse trucks dump
their entire load into the large hopper on
one side of the machine. The operator raises
the hopper to load the first compacting
chamber. A platen compresses and forces the
material into a smaller chamber where a
second platen and a shear plate compress it
still further. Two additional rams compress,
the bale from the smaller chamber. At the
same time a wheel-type trenching unit on
the opposite side of the machine excavates
a trench 42 in. wide and up to 8.5 ft
deep. The machine compacts fill material
and levels off the area using a large dozer
blade.
65-0615
Stirrup, F. L. Controlled tipping. In
Public cleansing; refuse disposal. Oxford,
The Institute of Public Cleansing, 1965.
p.16-47.
Precautions must be taken in controlled
tipping. Refuse should be deposited in
layers with each layer covered with dirt.
Avoid depositing in water and prevent fires
or vermin breeding. Temperature should
reach 150 F to kill pathogens. A site
should be selected on the basis of: its
depth, land restoration and improvement,
length of haul, winds, its life and future
use. In U.S. area required is one acre
per 10,000 persons per year. Site operation
depends on sound roadway construction,
buildings, topsoil, and drainage work.
Trench fills and bulldozers are used. A
site may be difficult because it is
waterlogged and must be drained, a deep
valley, or it consists of sand or clay.
Any inert material which will pack
reasonably well can be used as cover.
To control pests, have the cover prevent
the penetration of food smell and gas the
area. Tipped land may be used as
recreation areas in the future. Have
a topsoil cover of 6 in. to support growth
of grass. The grass root should grow
for one year to prevent broken glass from
coming to the surface.
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0613-Ub21
650616
Texas hauler operates fill jointly with
municipality. Refuse Removal Journal,
8(3):18, 31, 38, 1-144, Mar. 1965.
Estes Service Co. and Tarrant County have
joined together to operate a sanitary
landfill outside of Ft. Worth. Before
the merger, refuse was deposited in open
dumps and burned. Estes Service has 32
trucks to service residential and commercial
areas in the county. A breakdown of the
locations and kind of the company's
538 containers is also given.
STREET CLEANING
65-0619
Bell, C. W. Stability and speed required.
American City, 80(7):48, July 1965.
The new truck-chassis type sweeper in
Neosho, Missouri, with 7,750 population is
described. The new sweeper claims higher
speed for trips to the dump, and greater
stability and maneuverability than the
conventional type it replaced, and also
had the ability to clean outmoded, but
still used, depressed gutters.
65-0617
Tracked vehicles for compaction.
Cleansing, 55(7):429, July 1965.
Public
A test in Dundee confirmed that wheeled
vehicles achieve better compaction than
tracked vehicles in sanitary landfill
operations. However, this difference in
degree of compaction was rather slight,
and the tracked vehicle had many advantages
economically and functionally. The
tractive effort could operate where a
wheeled shovel could not, and was also
immune to punctures.
65-0618
1200-acre landfill contractor began in
1932 using pick and shovel. Refuse Removal
Journal, 8(12):8-9, 18, 38, Dec.
1965.
The growth and management practices of
a large Chicago landfill contractor,
including description of operations at
present disposal sites are outlined. The
four landfill sites serve all areas of
the city and many of the suburban
communities, and are located in residential
areas. Plans have been made and implemented
to reuse the land after a landfill is
completed. Initial public opposition to the
landfills has subsided as former landfill
sites are used for parks, schools,
and apartment complexes. An extensive
public relations campaign succeeded in
getting land rezoned for a trench landfill.
All disposal sites are enclosed by a
cyclone fence. No salvaging is permitted,
and neatness around the landfill is
requisite. No burning is permitted
at any time.
65-0620
Cardiff cuts street sweeping costs by 50
percent. Public Cleansing, 55(3):129-133,
Mar. 1965.
Cardiff, Wales, a city of 264,000 with 328
miles of streets, reorganized their
collection of street sweepings from
mechanical and manual sweepers by using
strategically located 6 cu yd dumpster
containers. Originally 4 different
systems were being employed including
articulated vehicles at strategic points,
exchangeable bins located at sub-depots,
curb sweeping boxes which were periodically
emptied by a collection vehicle, and two
trucks which toured on planned routes.
Three years ago the cost of this system
was $12,000 per year. Then safe sites for
the dumpster containers were obtained at
suitable areas by congenial arrangements
allowing the property owners to use the
containers for their own refuse also. Two
dumpsters and 30 containers are now used
for collecting sweepings at one-half the
cost of previous systems, and the department
services have also been expanded.
65-0621
Danforth, H. L. How to keep gutters clean.
American City, 80 (7):48, July 1965.
Tucson, Arizona, has made a plea to shop
owners and their janitors to pick up early
morning store sweepings instead of
sweeping them outside into the gutter only
hours after sweeping by street machines.
The program, which is designed to make the
downtown more conducive for business, has
been emphasized by cards and signs.
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Street Cleaning
65-0622
Denison, R. E. Rate and up grade your
street cleaning. American City, 80(4) :120-
122, Apr. 1965.
In order to rate and upgrade street:
cleaning service, officials must become
familiar with job conditions and plan
accordingly, organize men and equipment
wisely, keep detailed records on their
work, make cleaning schedules flexible,
control parking by ordinance, balance
labor and machines, tell their council
exactly how much cleaning budgeted funds
will buy, stimulate the public's interest
in cleanliness, and up date sanitation
and anti-littering ordinances.
65-0623
Drasler, L. L. Management of street
sanitation operations. In American Public
Works Association Yearbook, 1965. Chicago,
American Public Works Association, p. 172-
175.
The management of street sanitation
operations in Cleveland is discussed,
noting equipment, new techniques, difficult
problems, and aid by legislation and
education. Proper and continuous planning
is necessary, and items to be evaluated
include: comparison of performance
between the districts, performance of each
individual sweeper, an unbiased, weighted
comparison of performance of sweepers of
different makes, effectiveness of
supervision and manpower, need for
replacement of equipment, and the possible
need for changing routes and/or working
schedules. Cleveland has 35 mechanical
sweepers; 10 flushers with leaf suction
attachment will eliminate much land labor.
Improved broom material (polypropilene
brush) is used. Savings without seriously
affecting services were achieved by
eliminating the assistant in the 2-man
sweeping operation and in the area of
equipment, In an effort to keep Cleveland
beautiful, a Clean-up Campaign is held
every Spring. The street cleaning program
in Cleveland is successful because of an
adequate budget for sufficient manpower
and equipment, workable anti-litter and
parking control ordinances and their
enforcement, and continuous pub Lie
education.
65-0624
50 brooms will sweep New York. Refuse
Removal Journal, 8(5):35, May 1965.
New York City has purchased 50 tank-like
mechanical brooms as part of its
anti-litter drive.
65-0625
Green, L. B. We vacuum and flush our
streets. American City, 80(5):104-105,
May 1965.
In Montgomery, Alabama, a vacuum device
was utilized to pick up an over-abundance
of grass, and it proved so effective
that it was used regularly. Formerly,
streets were swept with a standard motorized
sweeper, and the operator deposited the
sweepings on the street for collection. The
final step consisted of flushing to remove
the last traces of debris and dust. This
system required three vehicles, three
operators, and three laborers. By using
the vacuum cleaner followed by the
flusher only, two vehicles, two operators
and one laborer were needed. The Good Roads
Scavenger's 12-yd capacity permits it to
operate for a long period before dumping
becomes necessary. Impressed with the
results, the City Commission authorized
the purchase of three Good Roads
trailer-mounted vacuum Scavengers, and two
additional flushers. The city has been
divided into four sections with a foreman
in charge of each section. The vacuum
machines will clean 10 to 15 curb miles
a day and burn about 30 gal of gas daily.
Water tanks must be filled at least twice in
8 hr and the huge dust filters at the top or
the containers must be washed daily to
maintain peak vacuum efficiency. A
machine used for street cleaning should
have a vacuum system whereby the debris
bypasses the fan blades. Units may
include a sprinkler system to prevent
dust and to aid in compaction.
650626
Haff, H. Street cleaning involves more than
sweeping. American City, 80(7):100, July
1965.
The street sweeping program of Hempstead,
New York, with 1,650 miles of street
and 33 sweepers is reviewed. One
hundred thirty-five town-owned parking
lots are cleaned at night or early
morning. Plastic fiber is used in the
sweeping brooms, which are made by the
city. The city also operates a small
asphalt plant to patch road cuts by
utilities.
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0622-0632
65-0627
Hickok, R. Sweep sand with hickory.
American City, 80(4):48, Apr. 1965.
El Paso, Texas, has switched back to
hickory on the brooms of sweepers after
an unsatisfactory trial with synthetic
fibers. The apparent move against the
trend elsewhere is attributed to the
unusually heavy accumulation of sand which
blows into El Paso's streets.
65-0628
Mechanical sweeping. Public Cleansing,
55(7) :427, July 1965.
In a small city with a single street
sweeping machine it seems that a suction
type sweeper is preferred in spite of
its higher initial cost, as compared with
a 'sweeper-collector.' The advantages
of such a suction machine are that it can
lift wet or dry leaves from the
pavement, and that it has fewer
moveable parts which makes it less
subject to breakdown.
65-0629
A part-time street sweeper.
City, 80(4):48, Apr. 1965.
American
The village of New Carlisle, Ohio,
converts a multiple-use tractor to a
part-time sweeper by replacing the bucket on
the loader with an M-B LP Hydro pick-up
sweeper.
65-0630
Pratt, L. C. Flush before sweeping
for cleaner streets. American City,
80(3):118-120, Mar. 1965.
A description of the street-cleaning
operation of Minneapolis, Minnesota, is
presented. In spring, flushers wet down and
wash the winter's accumulation of dirt
to the side of the street to allay dust
from sweeper collection; in fall, flushers
dampen and soften brittle leaves so that
sweepers can collect them in one pass.
Occasionally, flushers are sent out to
dampen loose chips resulting from seal
coating before sweepers tackle them.
Methods the city has employed to counter
the parking problem and the city's street-
cleaning fleet are described.
65-0631
Scottish center discuss mechanical street
cleansing. Public Cleansing, 55(2):119-124,
Feb. 1965.
Different types of sweeping machines were
compared. Larger street cleaners, 6 ft
wide were less maneuverable than the
smaller 4 ft types in urban streets with
parked cars, Transfer loading could
remove the disadvantage of small capacity
in the smaller machines. Suction-type
machines have higher capital and lower
maintenance costs than brush-type sweepers.
Many suction-type sweepers had a relatively
lower sweeping rate, but introduction of
a separate engine for suction not only
gave variability in speed, but also
allowed use of duty-free fuel for the
auxiliary engine. Tests upon polypropylene
brush fibers have shown them to give
satisfactory use and long life. Footpaths
should be washed manually to avoid
water in shop doorways and cellars. Men
could pick up footpath litter in heavy
pedestrian traffic more easily than a
mechanical sweeper. Night use of
mechanical sweepers in suburban areas
must be limited because of noise and
parked cars. It was suggested to base
equipment comparisons on cost per thousand
sq yd swept. Anomalies in Scottish
licensing laws concerning street cleaning
were also discussed.
65-0632
Sherrill, C. A. We designed and built
our own leaf loader. Public Works,
96(6):133, June 1965.
A Clark-Lynn leaf loader is described
which was used to cut total leaf collection
time in half in Mooresville, North Carolina.
Advantages considered are that the vehicle
operator had positive control over the
nozzle; the need to connect and disconnect
a loader for each load was eliminated;
and the workmen were readily visible
to the driver. The leaf-loader design which
was adopted makes use of a V-type, 4-cylinder,
VH4D, 30-hp aircooled-Wisconsin engine
for power. The unit is mounted on the
right-front of the truck. Power is
transmitted to the blower through the
clutch and V belts. The suction unit,
made by Carolina Blower Company, has a
30-in. diameter and heavy-duty steel
plate casing. The impeller has six
heavy-duty reinforced blades. The loader
is mounted on an M-B packer body. The
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Street Cleaning
duck extends through the packer body and
compactor blade, permitting large loads
to be carried since the leaves can be
compacted. The nozzle pivots about a
horizontal axis and may be raised and hooked
in a travel position above the pavement.
Attaching the loader to the vehicle is
not difficult and it is stored on a
table with dolly wheels. It is locked
into place by dropping two pins through
matching holes in the pipes welded co the
front chassis. The leaf pick-up is from
the left front, the operator facing
oncoming traffic and having a clear vision
of traffic as well as a close-up view of
the nozzle. The device is patented and
several have been sold.
65-0633
Smith, W. H. Maggie modernizes Mishawaka's
methods. American City, 80(6):124-125,
June 1965.
A vacuum cleaner for leaf collection
was purchased by the mayor of Mishawaka,
Indiana. A schedule was publicized and
citizens were asked to keep their cars
off the street when their block fell due.
For the first time, home owners were
encouraged to rake the leaves into the
gutter where the machine could collect
them quickly. Flogging from leaf-
clogged inlets disappeared. The air
remained clear of smoke from smoldering
leaves. Costs dropped to a fourth of the
former value.
65-0634
Streamlining leaf removal operations.
Public Works, 96(9):92, Sept. 1965.
An Ohio city uses a Vac-Master vacuum
leaf machine that cuts time and cost of
leaf removal. A grinding mechanism
reduces the bulk of the leaves by about
one third.
65-0635
Street cleaning and planting operations
in San Francisco. Public Works, 96(6) :92,
94, June 1965.
The Bureau of Street Cleaning and Planting
of the San Francisco Department of Public
Works is responsible for the cleaning
of 1,657 curb miles of streets and 109
curb miles of traffic islands. The
Bureau is also charged with the maintenance
of street trees and landscaping, and the
landscaping of three sewage treatment
plants and other areas, for a total of
7,300 trees and 232 acres of landscaping.
During 1963 to 1964, the Bureau had 379
employees in two divisions and expended
$3,081,226. The street cleaning division had
71 units of motorized equipment. The
street cleaning division hauled over
100,000 cu yd of refuse to the sanitary
fill dump during the year. The Bureau
logged 20,054 radio calls over Public
Works Station KME 327, of which 13,110
were originated by the Bureau of Street
Cleaning and Planting. All emergencies
reported to or observed by the Department
can be acted on immediately. Two years ago,
gang sweeping in the south of Market
area was eliminated and a night mechanical
sweeper was substituted, but gang sweeping
was later re-activated because of the
increasing number of complaints from the
public. In order to clean this area
properly, both methods of cleaning were
found necessarv.
65-0636
Sunquist, S. Street cleansing and snow
clearance in Stockholm. APWA [American
Public Works Association] Reporter,
32(2) :12, 16-17, Feb. 1965.
In Stockholm, streets are cleaned by
both machine and hand daily on a rotating
basis by limiting parking. In winter
Stockholm has a contract for 24 hr weather
forecasts with extra reports for sudden
changes. A gritting organization,
with 13 one-man trucks are on around-the
clock-basis from November 1 to April 1,
each assigned a specific district. If
conditions worsen, 29 city and 51 private
trucks are leased. They hold 2.2 cu m of
grit which is spread in front of the driving
wheels. This gritting operation is
controlled by the driver. Tests show that
the most economic sand is 3 to 4 percent
salt by weight. Salt must be examined
as it may damage vegetation, concrete, or
animals; 10 percent salt by weight is used
on thin ice coatings and pure salt on
steep slopes. Stockholm uses straight or
rock salt at the start of snowfall and places
boxes of sand and salt mixture throughout the
city. Winter snowfall averages 100 cm.
For fast street snow removal, the Stockholm
Cleansing Department uses supplement
equipment and drivers, which keeps capital
and garage space at a minimum. Because
of traffic conditions most snow is put
into piles equivalent to two parking spaces.
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0633-0641
It is then usually dumped into the sea.
Total equipment used last year was 100
plows, 80 gritting and 200 hauling
trucks, 170 tractors, 90 graders, and 200
loading machines.
65-OS37
Untouchables strike in New Delhi, India.
Refuse Removal Journal, 8(3) :2S, Mar.
1965.
Eight thousand untouchables who work as
street sweepers in New Delhi, India, went
on strike. An untouchable is the lowest
rung in India's ancient caste system, and
it is unthinkable that they would attack
the order of things. Most of the sweepers
dropped their short broom of bound twigs to
support demands for higher pay and better
uniforms. The average laborer earns the
equivalent of $10 per month. Mien work
stopped, refuse began to accumulate in
the streets, and striking sweepers hauled
litter into the streets to help their
cause. Roving bands of sweepers attacked
non-strikers. The New Delhi Municipal
Workers' Union supported the strike. The
government declared sweeping an 'essential
service' protected by law, and arrested
24 strike leaders under the Defense of
India Rules, in an effort to get the
men back to work. The sweepers continued
to fight, six going on a hunger strike,
while refuse mounted in the streets.
Finally city officials agreed to discuss
the demands, and work was resumed.
65-0638
Woodward, R. C. Why wire" Public
Cleansing, 55 (10):571-574, Oct. 1965.
Recent advances in street cleaning brushes,
with particular emphasis on wire brushes
are described. In sweeping efficiency
tests, wire brushes out-performed natural
fibers. In economy tests, wire cost
$0.09 per mile swept compared to
$0.18 per mile frr natural fibers. Steel
brushes require greater emphasis on
proper brush pressure and adjustment to
realize greater economy. Wire brush life
is about 500 to 1 ,000 miles compared with
50 to 100 for natural fibers. Relative
costs and mileages of various natural,
synthetic, and crimped-xrire brushes are
compared.
EDUCATION AND RESEARCH
650639
Bel], J. M., and E. A. Glysson. Academic
education and training in solid wastes. In
Proceedings; Technical and Planning
Aspects of Solid Wastes, Columbus, Sept.
19fi5. Ohio Department of Health. p.W-3
to W-28.
The information gathered from a questionnaire
sent to 107 colleges and universities
in the United States and Canada (from
which 91 (85%) replies were received) showed
that only 8 (9?) were presently conducting
research on solid wastes and only 11
(13%) expect to start research in the
near future. Only $134,000 was appropriated
for research, most of it from the USPHS.
Only 3 (3%) of the institutions were offering
courses on solid waster- and 5 (6%) expect to.
Tlie comments made on the questionnaires
with regard to the academic position of
solid waste are given. The problems
of keeping up with research developments,
with innovations. and with economic
changes are described. Questions about
specific courses and the students taking
them were answered. Some chemistrv and
physics majors have taken courses in
solid waste disposal although most of the
students are in engineering.
65-0640
Chappel, W. California school starts
course on solid wastes. Refuse Removal
Journal, 8(2):36, Feb. 1965.
The Engineering College of U.C.L.A.
will inaugurate a 10-week seminar in
Solid Waste Technology. The lecturers will
be authorities in their respective fields.
65-0641
Comprehensive research needed for public
cleansing service. Surveyor and Municipal
Engineer, 125(3809):38-40 , June 5, 1965.
In a paper entitled 'Specialization and
Research in the Larger Units of Local
Government' , given at the annual conference
of the Institute of Public Cleansing at
Scarborough in June of 1965, R. I. Cooper
noted the large sums spent on pure and
applied research by industry, but that
the cleansing industry which expends 87
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Education and Research
million in England and Wales annually
spends practically nothing on research. An
example of the need for research is the
refuse storage situation which has
actually changed very little in the last
century. The storage of putrescible
refuse in dustbins or other containers
for up to a week before collection is out
of place in the space age. As
alternatives to storage of putrescible
refuse on the premise are: a water-borne
system such as the Garchey System for
transporting the refuse from the house to
a collecting point. Progress in this
field has been slow, but a research unit
might accelerate the advancement of the
method if it has merit. On-site refuse
incineration is regarded as the obvious
solution now that the smoke and odor
problem has been solved. There are
similar problems in the fields of disposal,
work stud^, and street cleaning, which
could be helped by suitable research.
Of all the alternatives that have been
considered, the most practical and the
one which offers the most promise of
immediate results is that of a research
section within each large cleansing
department. Units such as these could
develop into regional research centers
and hopefully into a national research
center in time.
65-0642
Cooper, R. I. Discussion on 'Specialization
and research in the larger units of local
government'. Public Cleansing, 55(8):
446-451. Aug. 1965.
The discussion brought out the need for
knowing why there was a lack of
regionalization and research, the possible
assistance of universities in researching,
the use of extensive research before
regional disposal councils were set up,
and highlighting of research and
development which has been done by Local
departments.
65-0643
Current solid waste research projects.
Journal of the Sanitary Engineering
Division, American Society of Civil
Engineers, 91(SA6):13-16, Dec. 1965.
Brief reviews of 15 current research
projects on solid waste disposal subsidized
or financed by Public Health Service
grants are reported. Research is being
conducted in the fields of sanitary
landfill utilization, computer programming
of refuse collection systems, pyrolysis
of municipal refuse, incinerator residue,
shipborne municipal incineration,
continuous municipal incineration,
composting fruit and vegetable refuse,
livestock and farm waste studies,
incineration of radioactive solid waste,
and planning of a national solid waste
management conference.
65-0644
Eldredge, R. , and J. Vanderveld.
Non-academic education and training. In
Proceedings; Technical and Planning Aspects
of Solid Wastes, Columbus, Sept. 1965.
Ohio Department of Health. p.X-1 to X-25.
Non-academic education is specifically
designed for the decision-makers and the
doers. Decision makers are those who hold
positions of administrative responsibility:
mayors, city councilmen, public works
directors, superintendents of sanitation.
Planners and consulting engineers are
'decision-makers' and non-academic education
may be as important to them as academic
education. Doers, the men who do the
operation, appreciate knowing the problems
of decision-makers' problems. It helps
them realize the full responsibilities
of their jobs. Demonstrations of such
things as sanitary landfills, tours of
well-operated landfills, short courses on
specific subjects and correspondence courses,
are among the means of non-academic
education available. The problems of public
education are discussed. In-service
training is important and some examples
extramural program, which involves support
to individual investigators in universities
or other institutions for non-directed
research and is generally known as the
research grants program. Research grants,
often referred to as 'non-directed'
research, are based on a research idea
originally conceived by the investigator
which is submitted to the Public Health
Service for appraisal and possible
support. Presently there are 15 active
research projects in the solid wastes field
supported by the division. Eight active
grants dealing with municipal waste are
concerned with: sanitary landfill,
mathematical simulation of refuse
collection and disposal systems, pyrolysis
of municipal refuse, incinerator residue,
systems analysis for shipborne municipal
incineration, pyrolysis of solid municipal
wastes, and continuous incineration of
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Health and Safety
0642-0651
are given. Informing the worker of his
part in the total scheme creates morale.
65-0645
$197,500 granted Harvard U. for
incineration at sea. Refuse Removal
Journal, 8(10):38, Oct. 1965.
The U.S. Public Health Service has
awarded a $197,500 grant to Harvard
University's School of Public Health for a
two-year study of refuse incineration
and disposal at sea.
65-0646
Public Health Service to give three
solid waste courses. Refuse Removal
Journal, 8(10):18, Oct. 1965.
The Public Health Service will offer three
short training programs in solid waste
technology: Solid Waste Orientation,
Technical and Planning Aspects of Solid
Wastes, and Survey of Solid Waste Service.
and Planning Aspects of Solid Wastes,
Columbus, Sept. 1965. Ohio Department
of Health. p.Z-2 to Z-18.
The Division of Environmental Engineering
and Food Protection provides consultative
and technical assistance to state and
local health departments, universities,
and other agencies in planning and
developing a program in the field of
environmental engineering and food
protection. The accomplishment of these
programs requires: the identification
and assessment of environmental problems,
the development of control methods, and
the application of knowledge obtained.
The Division has two types of research
activity: the intramural program, which is
concerned with research usually conducted
by the Public Health Service, and the
municipal refuse. Six projects currently
active related to industrial and farm
solid wastes deal with canning operations
in the food industry, agricultural wastes
including animals waste problems, and
vector control projects. The contract
number, project manager, address,
allocation, and a brief abstract
of the projects are given.
65-0647
Research Grant. Public Cleansing,
55(4):220, Apr. 1965.
Research grants totaling $100,000, have
been awarded to British schools to study
the processing of household and industrial
wastes into utilizable and harmless products,
and the use of microorganisms on preparing
trade effluent, such as canning and other
food wastes, for utilization or sanitary
disposal.
65-0650
University course on solid wastes.
American City, 80(1):107, Jan. 1965.
The University of West Virginia is offering
a course on solid waste disposal as part
of its air-pollution-control graduate
training program. The program is
supported by a training grant from
Division of Air Pollution.
65-0648
61 attend 10-week solid waste technology
course at U.C.L.A. Refuse Removal Journal,
8(6):16, June 1965.
The Engineering Extension division of
UCLA sponsored a 10-week lecture session
in Solid Waste Technology. Sixty-one
students enrolled in tbe course, which
briefly covered all phases of solid
waste collection and disposal.
65-0649
Steed, H. C.
engineering.
Research in solid waste
In Proceedings; Technical
HEALTH AND SAFETY
65-0651
Arkansas State Department of Health.
Proceedings; First Conference, Recreation
Sanitation and Safety, Little Rock,
May 25-26, 1965. Dallas, U.S. Public Health
Se*~_ce. 97 p.
The conference was sponsored by the
Arkansas State Department of Health in
cooperation with the U.S. Public Health
Service. The objectives of the conference
were to: develop an awareness within
Arkansas of the environmental health aspects
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Health and Safety
of planning, developing, operating, and
maintaining outdoor recreation areas; to
emphasize the role of the Arkansas
State Department of Health in recreation
sanitation and safety; and to unite the
numerous aspects of the recreation
environment that relate to both sanitation
and safety. The papers presented covered
such topics as: recreation safety in
water sports, travel trailer parking areas,
water supplies, sewage disposal, plumbing
and heating, food sanitation, vector
control, and refuse handling.
65-0652
Axtell, R. C. Comparative toxicities of
insecticides to house fly (Musca domestica)
larvae and Macrocheles muscaedomesticae,
a predator of the house fly. In
Integrated control of the house fly.
Raleigh, North Carolina State University,
Aug. 2, 1965. p.1-5.
The comparative toxicities of 17 insecticides
to house fly larvae and a common manure-
inhabiting macroshelid mite were determined.
The LD/50's and LD/95's for the 17
insecticides were determined for third-
instar larvae of the house fly and adult
female Macrocheles muscaedomesticae, a
predator on house fly eggs and larvae.
The mites and fly larvae were exposed to
the insecticides incorporated into fly
rearing medium. Bayer 39007 (2-
isopropoxyphenyl methylcarbamate) ,
Ciodrin alpha-methylbenzl 3-hydroxycrotonate
dimethyl phosphate), dimethoate and
demetilan were more toxic to the mites than
to the fly larvae. Kepone
(decachlorooctahydro-1, 3,4-metheno-2H-
cyclobutarc d]pentalen-2-one), lindane,
coumaphos, ronnel and GC 9879
(alpha(diethoxyphosphinothioylthio)
gamma-butyrolactone) were more toxic to
the fly larvae than to the mites. The
remaining chemicals which were about
equally toxic to the fly larvae and the
mites were: naled, dichlorovos, fenthion,
malathion, trichlorfon, DDT, diazinon and
chlordane. The development of selective
insecticides is advocated in order to make
possible an integrated house fly control
program.
65-0653
Axtell, R. C. Integrated control of the
house fly. Raleigh, North Carolina State
University, Aug. 2, 1965.
In order to develop an integrated control
program for the house fly, better knowledge
of the behavior and insecticide-
susceptibilities of the mite and insect
enemies of the house fly is required.
Results of investigations of the behavior
and insecticide-susceptibilities of
manure-inhabiting mites, which are
predacious on the eggs and larvae of the
house fly are reported. Research
accomplishments are presented in the
form of sub-projects. The complete
manuscripts and reprints of these
reports are included: Phoretic Relationship
of Some Common Manure-inhabiting
Macrochelidae (Acarina: Mesostigmata)
to the House Fly; Predation by Fuscuropoda
vegetans (Acarina: Uropodidae) on the
House Fly (Musca domestica); Sensory
Functions of the Palps and First Tarsi
of Macrocheles Muscaedomesticae (Acarina:
Macrochelidae), a Predator of the House
Fly; Manure Substrate Effect on the
Phoretic Behavior of Macrocheles
Muscaedomesticae (Acarina: Macrochelidae);
and Comparative Toxicities of Insecticides
to House Fly (Musca Domestica) Larvae and
Macrocheles Muscaedomesticae, a predator
of the House Fly.
65-0654
Axtell, R. C.. and D. J. Parish. Manure
substrate effect on the phoretic behavior
of Macrocheles muscaedomesticae (Acarina:
Macrochelidae). In Integrated control of
the house fly. Raleigh, North Carolina
State University, Aug. 2, 1965. p.1-11.
Macrocheles muscaedomesticae (Scopoli)
is a significant biological agent
regulating house fly populations and along
with other manure-inhabiting mites must be
considered in the development of an integrated
control program against the house fly. The
mite was exposed to adult house flies
in the presence of various substances.
The frequency of phoretic attachment to
the flies increased in the presence of
manure (chicken and cow) of increasing
age. Conversely, the detachment of the
mites from their fly hosts decreased in
frequency as the manure aged. The
attractiveness of fresh manure was
demonstrated, but could not be explained on
the basis of ammonia vapors since the
mites were not attracted to urea, ammonium
nitrate and ammonium hydroxide in an
olfactometer. An artificial fly rearing
medium was not attractive to the mites
and did not induce increased frequency of
phoresy as it dried. The attractiveness of
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0652-0658
manure decreased upon drying but was
restored with re-moistening. It was
concluded that phoretic attachment takes
place when the manure attractiveness is
less than that of the flies and detachment
occurs when the manure attractiveness
exceeds that of the flies.
650655
Axtell, R. C. Phoretic relationship of
some common manure-inhabiting
macrochelidae (Acarina: Mesostigmata)
to the house fly. In Integrated control
of the house fly. Raleigh, North
Carolina State University, Aug. t, 1965.
Several species of Macrochelidae (Acarina:
Mesostigmata) commonly occur in domestic
animal manure. These mites are predaceous
on the eggs and first-instar larvae of
the house fly, Musca domestica L., and
cause substantial reductions in house fly
production from manure. A series of
experiments was conducted to determine
which of the five common manure-inhabiting
Macrochelidae are phoretic on house flies.
House flies, Musca domestica (L.), were
trapped from mite-infested dairy cattle
manure and collected by net inside dairy
barns. Macrocheles muscaedomesticae
(Scopoli) and M. Subbadius (Berlese)
were commonly found attached to the house
flies. Although M. Medarius (Berlese),
M. robustulus (Berlese) and Glyptholaspis
confusa (Foa) were present in the manure,
only one specimen of each of the first
two species and none of the third were
found attached to a house fly. In a
comparison of the behavior of macrochelids
from laboratory colonies, M.
muscaedomesticae and M. subbadius were
phoretic on the house fly and the other
three species were not. As a prerequisite
to possible manipulation of predaceous mite
populations as a means of house fly control,
additional data are needed on the role of
Coleoptera and Diptera as carriers of
macrochelids. (Reprint)
65-0656
Edwards, P. R. Salmonellosis--an
expanding problem. In Proceedings;
National Conference on Salmonellosis,
Atlanta, Georgia, Mar. 11-13, 1964.
Public Health Service Publication No. 1262.
Washington, U.S. Government Printing
Office, Mar. 1965. p.7-12.
Improved diagnosis and increased awareness
of salmonella infections are partially
resDonsible for the increased number of
cases recognized; yet reporting of the
actual incidence is still quite incomplete.
Recognized types of salmonellosis have
grown from 44 in 1934 to well over 800
at the present, and previously unrecognized
serotypes have been appearing at the rate
of 50 to 80 a year. The intensified search
for the presence of salmonellae has led
to their discovery in unsuspected
environments, such as in the intestinal
tract of some reptiles, and in foods of
vegetable or marine origin. The contamination
of foods of animal origin can be reduced
by such practices as thorough cleaning
of abattoirs and treatment of carcasses.
Heating, acidification and heating,
and alkalinization have been recommended
for destruction of salmonellae in egg
products. However, in investigations,
the food responsible for infection could
be Identified in only 12 percent of the
outbreaks, and it is not always the
originally contaminated food that gives
rise to infection. Almost half the
outbreaks of salmonellosis occurred in
hospitals. Whether or not the character
of the hospital diet accounts for this high
proportion should be investigated. Human
carriers create a problem which might be
alleviated by regular fecal examination
of food handlers in hospitals and geriatric
institutions. Finally, more positive
action should be taken to eliminate
salmonellae from animal feeds.
65-0657
Environmental health practice in recreational
areas. Washington, U.S. Government
Printing Office, 1965. 134 p.
All aspects of environmental health
practices are discussed in reference
to the planning, operation, and maintenance
of recreational areas. Individual chapters
deal with sewage disposal, refuse handling,
and stable maintenance, while others touch
on problems of solid waste handling and
disposal for campgrounds, picnic areas,
and restaurants. Explanations are included
of types of sewage treatment and refuse
disposal methods.
65-0658
Parish, D. J., and R. C. Axtell. Sensory
functions of the palps and first tarsi
of Macrocheles muscaedomisticae (Acarina:
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Health and Safety
Macrochelidae), a predator of the house
fly. In Integrated control of the house
fly. Raleigh, North Carolina State
University, Aug. 2, 1965. p.1-10.
Macrocheles muscaedomesticae (Scopoli)
is a manure-inhabiting mesostlgmatid
mite, predaceous on the eggs and first-instar
of the house fly. It has generally been
assumed that the first pair of legs of
Macrochelidae perform sensory functions,
but neither the function of the legs nor
the palps has been established experimentally.
650659
Hosel, C. Waste disposal from the viewpoint
of public health. In Refuse and waste disposal.
Berlin, Druckhaus Lichterfeld GmbH, 1964.
p. 1-21.
The historical relation between municipal
sanitation and general health is reviewed.
Municipal sanitation is one of the main
concerns of the public health service. It was
only in the 19th century that effective measures
were initiated in this field. This was due
mainly to scientific and technical progress,
political and social changes , and introduction
of a public health service. Collection and
transport of refuse and final disposal of
solid waste are discussed. Refuse may be
utilized or may be disposed of by dumping,
incineration, or composting.
650660
Klotter, H. Disinfection and devitalization
of solid and liquid waste. In Refuse
and waste disposal. Berlin, Druckhaus
Lichterfeld GmbH, 1965.
Disinfection of waste, devitalization
of waste, and parasite control are
discussed. Sterilization of waste with
chemicals, chlorine, chlorine dioxide,
ozone, ethylene oxide, and other reagents
are presented. Sterilization of waste
by physical methods such as thermal
waste treatment including incineration,
UV irradiation, and electrolytic waste
sterilization are discussed. The physical
worm egs control methods, and the
biological worm egg control methods are
two methods of parasite control.
65-0661
LeSage, F. Trained personnel avoid
hazards of industry. Refuse Removal
Journal, 8(1):30, Jan. 1965.
The new compaction truck has its own peculiar
hazards, which can be overcome by safety
training programs including various
types of emergency drills and good
selection of personnel. To date there
are no such programs and this lack
accounts for the high rate of accidents.
65-0662
Nix, H. L., and C. J. Dudley. Community
social analysis of Savannah-Chatham
County. Series 1. Atlanta, Georgia
Department of Public Health, May 1965.
51 P.
A community analysis of Savannah and
Chatham County, viewing the community
through the eyes of those who by virtue
of their positions are in a position to
know a great deal about their community,
is presented. Regular interviews were
held with twenty-seven positional and
reputational leaders. In addition to the
interviews, twenty-three of the respondents;
completed a questionnaire. The questions
used in the study were designed to elicit
information concerning the following:
basic attitudes and values in the
community; community efforts; community
needs and problems; ratings of community
services; areas of cooperation and
opposition; community organizations; and
community leadership. The information
has been gathered in order to provide
information, understanding and consultation
to the sponsors of the Environmental
Health Studv which should result in more
adequate implementation of acceptable
environmental health recommendations.
650663
O'Donnell, A. E., and R. C. Axtell.
Predation by Fuscuropoda vegetans
(Acarina: Uropodidae) on the house fly
(Musca domestica). In Integrated control
of the house fly. Raleigh, North Carolina
State University, Aug. 2, 1965.
Uropodid mites are generally considered
to be fungus feeders. However, it has
been reported that uropodid mites occurred
frequently in samples of manure of dairy
cattle and chickens collected from inside
barns in New York State. A study was
undertaken to compare the rates of predation
on eggs and first-instar larvae of the
house fly by deutonymphs and adults
of both sexes of F. vegetans to predation
by adult female M. muscaedomesticae. M.
Muscaedomesticae used in the study were
from mass cultures maintained on a cow
manure substrate with house fly eggs
added daily. F. vegetans were collected
from chicken and cow manure 2 weeks prior
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0659-0667
to the initiation of the study and were
maintained on cow manure and house fly
eggs until used in the experiments. Both
sexes of adult F. vegetans were found to
he predaceous on the eggs and first-
instar larvae of the house flv, although
at a lower rate than adult female M.
muscaedomesticae. The difference in
predation between the sexes of F. vegetans
was not significant. F. vegetans deutonymphs
were predaceous on the eggs and first-
instar larvae of the house fly but at a
significantly lower rate than adult female
M. muscaedomesticae. In the feeding
preference test, M. muscaedomesticae fed
more on the fly eges than on the larvae,
while the converse was true for F.
vegetans. The data obtained in the
experiments indicate that adults of F.
vegetans are predators of the house fly
but to a lesser extent than adult female
M. muscaedomesticae. The predation by
the two species ought to be complementary
when they co-exist in manure. (Reprint)
650664
Overweight 55"gallon drum amputates fingers
and toes. Refuse Removal Journal,
8(1):24, Jan. 1965.
The 55"gal refuse drum accounts for numerous
types of injuries to sanitation laborers
as well as increasing collection operating
costs in Araarillo, Texas. Forty-four
thousand of the 61 ,200 trash receptacles
are the 55-gal drums.
650665
Perlstein, J. Pictorial keys to common
domestic flies in California. California
Vector Views, 12(5): 21-24, May 1965.
A pictorial key with explanations to aid
in identifying common domestic flies and
their larvae particular to California is
presented. Correct identification of pest
species is the first step towards
managing control. The mere presence of
adult flies at a suspected breeding place,
disposal area etc., without identification
of their larvae is inconclusive. The
use of the pictorial keys and the
preservation of specimens is briefly
explained.
65-0666
Proceedings; National Conference on
Salmonellosis, Atlanta, Ga., Mar. 11-13,
1965. Public Health Service Publication
No. 1262. Washington, U.S. Government
Printing Office, Mar. 1965. 217 p.
This booklet contains the proceedings of
the National Conference on Salmonellosis
which took place March 11 to 13, 1964,
in Atlanta, Georgia. Over 200
representatives from State and Federal
agencies, industry, and universities
attended. This monograph includes the
formal papers presented and the pertinent data
reported during the several discussion
sessions. The welcome address was given
bv Dr. David E. Price; Dr. James L.
Goddard outlined the purposes of the
conference. The topics discussed were:
'Delineation of the Problem,' 'Population
at Risk,' 'Sources of Salmonella,' 'Interstate
Outbreak of Salmonella Derby Gastroenteritis,'
and 'Control of the Salmonella Problem.'
The banquet which followed the conference
was addressed by Dr. W. Charles Cockburn
on 'Salmonella, Retrospect and Prospect.'
A listing of conference participants and
participating organizations is given.
65-0667
Protective clothing. Report of the
Research Committee 1965. Institute of
Public Cleansing, 1965. 6 p.
The purpose of the guide for protective
clothing is to define suitable scales
of issue for each kind of work and to
recommend a specification for each item
of equipment in order to simplify
competitive tendering. The scales which are
tabulated are offered more as a standard
for comparison than a firm recommendation.
The following matters should be taken
Into account when considering the provision
of protective clothing for employees:
expenditure on well designed clothing
may be fully recovered as a result of
improved health of the recipients; the
expenditure may also be partly offset by the
reduction or even elimination of working
time lost; a good uniform may mitigate the
recruiting difficulties which stem
from the poor social status of public
clenasing employees; the issue of clothing
should be complemented by provision of
lockers, drying room for wet clothes, and
the washing, dry cleaning, and repair
of all clothing at appropriate intervals.
The Scales of Issue cover various types
of employees such as inspectors, refuse
collectors, drivers, refuse plant
handlers, and tip men; the types of clothing
needed including uniforms, footwear, and
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Health and Safety
rainwear; and the normal period of
use that can be expected. Relevant
British Standard Specifications are
listed.
65-0668
Safety is a saving.
8(11) :12, Nov. 1965.
Refuse Removal Journal
Driver training, maintenance of
equipment, and incentive programs increase
truck safetv record.
650669
70,000 flies per cubic foot of garbage.
American City, 80(2):36, Feb. 1965.
A brief report on a Solid Wastes seminar
in Niagara Falls, New York is presented.
The talks touched on the propagation
of flies ia garbage, the growth of the
volume of refuse, how a sanitary landfill
should be operated, and the large amount
of unsanitary open dumps in New York
State.
65-0670
Sheppard, P. E. Accident rate highest for
trash workers. Refuse Removal Journal,
8(8) :26, 28, 56, Aug. 1965.
Sanitation workers have the highest accident
rate for all industries, with a record
of 72.39 disabling injuries per illion
man hours. This and other startling facts
and figures; were brought to light in a
recent survey conducted by the ational
Safety Council and the American Public
Works ssociation to determine the present
status of safety programs and accident
prevention efforts in the area of public
employees. Questionnaires were nailed
to 1,872 cities having 10,000 or
more population, considering the basic
questions of: does an accident problem
exist? If so, how serious is it0 What
is being done and what can be done to
meet the situation? Chart 1 summarizes
accident experience divided according to
population with an average of one out of
every 16 workers suffering a disabling
injury. In Chart 2, the Public Works
injury record is compared with the
National Safety Council's data on 41
major industries, showing definite room for
improvement. Chart 3 summarizes the
departmental accident rates. Chart 4
shows injury cost data, the average cost
for workman's compensation protection,
being $56.13 per employee per year.
Comnounded for all cities, this totals
$87,001,500, which is only for one type
of coverage. Additional costs are at
least equal to the cost of insurance.
Chart 5 shows the response received on
the materials used in the safety
program. Answers as to what is needed
to help a safety program were: provision
of literature, talks, films, posters,
etc. for public employee operations; the
development of training program guidelines
for supervisors and employees; the
provision of inforr,-;'" on public
employee safety programs and on accident
case histories, analysis, and collect
statistics.
650671
Slaughter of the rats. Public Cleansing,
55(5) -.275-277 , May 1965.
A rat control experiment conducted at
Tyseley, England, a refuse-disposal plant
handling 1 ,000 tons per week on a 5S. day
basis is described. To prevent migration
of the 4 to 5,000 rats when the plant was
closed down for a short time, a quick-kill,
single~dose poison was used. About 3,500
trays of Raticate Rat Killer were laid
out in several hours at various points. The
next day a large kill was observed,
estimated at almost 3,000 or 60 to 75
percent of the rats, with about: 3,000
bait trays being opened even though other
food was available. Evidence proved that
a rapid rate of kill was achieved, starting
within two hours after the bait was
laid. There was no danger to the operators,
and birds could eat the bait with no
adverse effects.
65-0672
Tips on flies on tips. Public Cleansing,
55(5) :292-294, May 1965.
Discussion of an English Sanitation board
held at Dudley is reviewed. Fly larvae
were observed in dust separated from
trash by screening before incineration,
and to avoid this nuisance it was recommended
that the dust be incinerated with
the other refuse. Insecticides were
dangerous and not completely effective
on piles of unincinerated dust. Short
comments on smoke, bonus schemes, and
abandoned cars are also included.
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0668-0677
65-0673
Weidner, H. House insect problems over
the centuries. Staedtehygiene,
16(4):83-88, Apr. 1965.
A problem which could not be solved for
centuries was the removal of wastes. All
garbage, trash, and rubbish including
excrements and animal carcasses were
dumped into open sewers, running through
the backyards of the houses, and very often
simply into the streets which were mostly
unpaved in those days. Beginning with the
year 1560 all streets had been cleaned
once every three months. Prisoners were
assigned to do this job. In the 17th
century a toilette emptying service
was established, but life in the city
continued to be everything else but
sanitary. The cities bred flies by the
millions and since the connection between
deadly diseases and the occurrence of
flies has been recognized only fairly
recently, nothing much was done about
them. With the improvement of the
sanitary conditions in cities the flies
disappeared, but only to concentrate on
waste disposal sites. Here the same snecies
have been found which formerly plagued
the cities. But other insects such as
locusts, cockroaches, and worms house
in the waste pile too. The fermentation of
the organic substances in the waste
(sometimes constituting up to 37% of
the entire waste) raises the temperature
considerably above the air temperature;
the prevailing humidity is constantly at
100 percent which makes it ideal,
especially for locusts. But the real
problem comes when they start to migrate
at the end of June to nearby homes, to
nibble at textiles and food and drive the
residents to despair with their chirping,
not to speak of the diseases these
insects spread. To solve this problem
completely the cities can only turn
to incinerating waste. (Text-German)
65-0674
WHO Expert Committee. Environmental
health aspects of metropolitan planning and
development. World Health Organization
Technical Report Series No. 297. Geneva,
World Health Organization, 1965. p.5-66.
Among the subjects discussed are: the
magnitude of the problem, planning for
environmental health, the objectives of
planning, the multi-purpose concept, the
conservation of resources, and the need for
social overhead capital. The problems
in metropolitan planning are discussed
and specific examples given from Russian
experience. Water supply, waste
disposal, drainage, solid wastes, and land
pollution, and air pollution are among
the specific problems of environmental
health surveyed. The administrative and
structural approaches are described.
Finally, research needs are outlined and
some suggestions made about training and
education. The role of WHO in these
matters is also emphasized.
LITTER
65-0675
The abominable litter man. Public Cleansing,
55(6):331-333, June 1965.
The 'Keep Britain Tidy Group' is behind the
anti-litter campaign which has very limited
effectiveness. Enforcement is the crux
of any litter deterrent, and this is what is
lacking both within the law and in any
voluntary anti-litter organization.
Educating the public and instilling community
pride can be a hope for the future, but at
the present there is an obvious lack of
civic concern with too much dependence
placed in governmental actions.
65-0676
Are your litter bins really necessary?
Public Cleansing, 55(12) :665-666 , Dec.
1965.
This editorial poses questions as to
whether the benefits of litter bins, in
terms of street cleanliness, bear any
relationship to the number of bins in a
particular district. It suggests that
other factors, such as popular litter
consciousness, have a greater influence
on street tidiness. It advocates a
closer cost-effectiveness evaluation,
taking into consideration original cost,
clean-out and maintenance of bins as well
as clean-up programs.
65-0677
Cincinnati wins clean-up contest. American
City, 80(4):105-107, Apr. 1965.
Cincinnati, Ohio, won top honors in a
national clean-up contest, sponsored
annually by the National Clean Up - Paint
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Litter
Up - Fix Up Bureau in Washington, I). C.
Prizes were also awarded to the top three
cities in eight different classes,
divided according to population. The
article describes the campaign of several
contesting cities.
65-0678
Deasy, C. M. Landscaping and litter control.
In American Public Works Association
yearbook, 1965. Chicago, American Public
Works Association, p.318-320.
'Beautifying' seeks to improve the physical
aspects by minimizing those qualities
that tend toward monotony or eliminating
those that are chaotic, and bringing a
sense of order and continuity to the
whole. Landscaping is one of the best
means of eliminating monotony. Methods
used to encourage the use of plant
materials include an annual 'Plant a
Tree Week' promotion on Arbor Day.
Similar methods of coaxing, educating,
and cajoling can be applied to litter
control. Litter control is a human
problem, and it is necessary to change the
mental attitudes of persons concerning
their city. People do have some
inhibitions about litter and their
inhibitions must be increased by instilling
a sense of community pride. The greatest
effort is being concentrated on the young.
Another objective is to facilitate
the disposal of litter. Convenient and
accessible litter containers are
necessary. A litter bag should be in
every car and a receptacle in every
service station so the bags can be emptied,
and a durable and attractive litter
container should be on every street
corner in commercial districts. While
an attractive receptacle is to be
preferred, the one essential quality is
that it be immediately recognized as a
litter container.
65-0679
The dirty face of a capital city.
Public Cleansing, 55(12):686-687 , Dec. 1965.
Sanitation conditions in Lima, Peru,
where carelessness and lack of public
spirit have generated large waste disposal
and street cleaning problems. Rubbish and
litter on roads and pavements, walls
filled with grease and half-torn posters,
broken-down motor vehicles exuding
grease and oil, and filthy fruit stalls
all contribute to an intolerable situation.
A new City Cleanliness Campaign hopes
to remedy this situation by engendering
more public spirit among the people.
65-0680
Duba, J. G. Beautification of American
cities-aided by urban renewal. In
American Public Works Association Yearbook,
1965. Chicago, American Public Works
Association. p.321-323.
The urban renewal program has done more
to contribute to the beautification of
American cities than any single program.
Conceived in the National Housing Act
of 1949, urban renewal was later
expanded from slum clearance to include
rehabilitation programs aimed at conserving
aging neighborhoods and communities.
Building code enforcement programs have
been included. The elimination of
slum and blighted areas has improved
the appearance of cities and has
eradicated conditions contributing to
crime and social problems. The
redevelopment of the cleared land has
improved housing conditions, provided
community facilities, increased the tax
base, and generated employment. Proper
planning of urban renewal projects can
contribute to the beautification of
cities, and examples are cited from
Chicago's 33 approved projects. In
new residential projects well-conceived
landscaping with open space has been
provided, shopping conveniently located,
signs minimized, and utility lines
placed underground. Older buildings have
been painted, accumulated debris removed,
and yards and parkways cared for.
Commercial centers have been designed
and developed to blend in with surrounding
residential communities, and traffic
problems have been alleviated. Adequate
parking has been provided. The
institutional development in Chicago, which
has probably contributed as much if not
more to the beautification of the city
as any phase of urban renewal, is
discussed.
65-0681
English roadside sanitary needs. Public
Works, 96(10):72 , 74, Oct. 1965.
An article by C. E. Waterfall in the
Royal Society of Health Journal, July-August
1965, is reviewed. Somerset County,
172
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0678-0685
England, has been plagued by the
inadequacy of sanitary facilities and the
unsatisfactory state of roadside rest
areas, all a potential public health
risk. Littering is prohibited by law,
although the Litter Act of 1958 is largely
ineffective due to lack of enforcement.
It is recommended that press, radio, and
television campaigns against littering
be renewed, that adequate litter receptacles
be provided, that roadside rest areas be
swept and maintained regularly, that
local provisions be made for the disposal
of large unwanted items, and that
enforcement he stepped up. The need for
toilet facilities is becoming acute, with
a critical need for adequate signs so that
available facilities will be recognized.
All roadside toilets should have parking
space. It is proposed that proper
sanitary and service areas be built and,
pending their completion, temporary
conveniences be provided in pairs, on
opposite sides of the road, at 20-mile
intervals. The permanent facilities should
have water and electricity and provisions
for washing. If sewerage is lacking, septic
tanks or prefabricated disposal plants
should be installed.
65-0682
Litter large and small.
55(2):67, Feb. 1965.
Public Cleansing,
The English Parliament's reluctance to
interfere with municipal disposal of
regular and also large waste articles
such as old cars is described. It was
felt that local authorities should make
provision for disposal of cars and
other bulky refuse brought to them, but
not necessarily to canvass for such
refuse. The availability of such services,
well advertised, would lower illegal
dumping of large refuse by residents.
65-0683
'Lively Louie' the talking litter basket.
Public Cleansing, 55(10):580-582 , Oct.
1965.
New York presently has 3 monitored
litter baskets with loudspeakers which are
controlled by operators with microphones
working from hidden vantage points. The
monitor encourages personally, in a
pleasant way, pedestrians to be litter
conscious.
65-0684
Pieces of debris whirl in space. Refuse
Removal Journal, 8(10):37, Oct. 1965.
Scientists estimate that there are over 300
man-made objects whirling around in
outer space. The Gemini-4 space voyage
added to this total when Astronaut
Edward White jettisoned some of his space
gear. Howard P. Jensen, secretary of the
National Council of Refuse Disposal
Association, stated that, 'One of these
days litter in space is going to create
quite a problem, and somebody must think
of a way to clean it up eventually, if
we're going to use outer space
extensively.' Among the space refuse
are a floating mass of 400 million
copper wires in a U.S. communication
experiment, old rocket hulls, and stray
parts of satellites.
MANAGEMENT OF SOLID WASTE
SYSTEMS
65-0685
Association of Bay Area Governments, Bay
Area regional planning program refuse
disposal needs study. Berkeley, Calif.,
July 1965. 19 p.
The present and future situations, costs,
regulations, and recommendations are
summarized. Collection and disposal
practices are discussed. Projected
population growth, refuse volume, and
disposal deficiencies from the basis for
future regional needs, graphs, tables, and
a map of disposal sites are provided.
65-0686
Association of Bay Area Governments, Bay
Area regional planning program refuse
disposal needs study; Supplemental
report. Berkeley, Calif., July 1965.
120 p.
The terms used in this supplemental
report are defined. Disposal methods
currently used are described. Past
reports which pertained to refuse
disposal in the San Francisco Bay
rea are summarized. The collection
and disposal practices of each county are
given. Tabular data is included.
173
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Management of Solid Waste Systems
Sections of the California Health and
Safety code pertaining to refuse collection
and disposal are summarized.
65-0687
Association of Bay Area Governments.
Alameda County. In Bay area regional
planning program disposal needs study-
supplemental report. Berkeley, Calif.
July 1965. p.21-33.
All disposal sites in Alameda County are
required to be operated as sanitary landfills.
Most refuse is collected by private firms
under contract or franchise with the
individual cities. Existing disposal
volume in the thirteen existing sites
will have been exhausted by 1981.
Residential collection is once or twice
weekly. Residential rates range from
$1.20 to $1.62 per cu yd. Fill and cover
is the most commonly used garbage is
cooked for hog feed. Data is given on
the collector, residential rate, refuse
type, refuse site, number of vehicles,
refuse tonnage—present and projected,
and capacities of existing sites.
program disposal needs study-supplemental
report. Berkeley, Calif. July 1965.
p.46-57.
Most refuse in Marin County is collected by
thirteen private collection services.
About 95 percent of the people in the
County are provided with garbage collection
service. Residential refuse is collected
once or twice weekly at a fee ranging
from $1.35 to $2.50 per month. There are
five major disposal sites, four of which
are privately owned. All are fill-and-cover
sanitary landfills. Three sites accept onlv
rubbish and demolition material. In
1963 there was a daily per capita refuse
production of 3.8 Ib. This statistic
does not account for individual disposal
or some industrial waste. The existing
8,300 acre ft in the present sites will
have been fully utilized by 1989. Data
is given on urban area population,
collector, collection rate, disposal
area, hauling distance, type of refuse,
landfill type, landfill owner, estimated
annual tonnage of refuse, projected
solid waste production, and capacity
of existing disposal sites.
65-0688
Association of Bay Area Governments. Contra
Costa County. Bay area regional planning
program disposal needs study-supplemental
report. Berkeley, Calif. July 1965.
p.34-45.
The county does not issue franchises or
establish collection areas. Disposal
sites may be located only in heavy
industrial districts. There are four
major sites; all are fill-and-cover
sanitary landfills. The existing volume
will have been utilized by 1982. By
the year 2000, the county will be
producing 975,000 tons or 1425 acre ft
of refuse annually. Residential refuse
is collected weekly; fees range from
$1.30 to $2.00 per month. Commercial
refuse collection is arranged. Cover
material for the landfills is obtained
from the site. Salvaging is practiced
at three sites. Data on area population,
collector, residential rate, refuse type,
disposal site, vehicles used, site
capacity, and projected refuse production
is given.
65-0689
Association of Bay Area Governments. Marin
County. In Bay area regional planning
65-0690
Association of Bay Area Governments. Napa
County. In Bay area regional planning
program disposal needs study-supplemental
report. Berkeley, Calif. July 1965.
p.58-66.
Six private agencies collect all the
refuse in the county. Residential refuse
is collected weekly at a fee ranging from
$1.00 to $200 per month. Four disposal
sites are operated by institutions, two,
by private companies, and one, by the
County. The County Health Department is
negotiating to have the four institution
sites county-operated or converted to
sanitary landfills like the other three.
Some burning is done at each site.
Cut-and-fill or area-fill methods are
used. Some salvaging is practiced. Per
capita refuse production was 1.8 Ib daily
in 1963. When municipal, agricultural,
and industrial wastes are added to the
garbage tonnage, the total waste material
amounts to 98,000 tons or 7.6 Ib per capita
per day. There is approximately 86 acres of
land available for disposal use, Assuming
no burning is done, this land will be
sufficient until 1973. Tabular data is
given on urban area populator, collector,
fee, disposal area, refuse type, vehicles
used, landfill type and owner, site
174
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0687-0694
capacity and remaining life, and projected
solid waste production.
65-0691
Association of Bay Area Governments.
City and county of San Francisco. In
Bay area regional planning program disposal
needs study-supplemental report. Berkeley,
Calif. July 1965. p.67-69.
Refuse collectors must have permits issued by
the Health Department. One private agency
collects from residential areas and the
other covers downtons. Weekly residential
backyard carry service is provided at $1.25
to $1.30 per month. Commercial refuse is
collected daily. The refuse collected is
disposed at a sanitary landfill near
Brisbane. A privately-owned site in the
city accepts only rubbish, demolition, and
construction material. During 1963 refuse
production was 750,000 tons. This volume
represents a daily per capita production of
5.5 Ib. Tabular data on projected solid
waste production is included.
65-0692
Association of Bay Area Governments. San
Mateo County. In Bay area regional
planning program disposal needs
study-supplemental report. Berkeley,
Calif. July 1965. p.70-84.
Eight companies collect refuse in San
Mateo County. Residential collection
rates range from $1.25 to $1.72 per
month for weekly collection. Approximately
98 percent of the population subscribe
to collection service. The average
one-way haul to disposal site is 1 to 8
miles. Five of fourteen disposal sites in
the county are publicly owned. Thirteen
sites operate as sanitary landfills,
utilizing fill-and-cover or cut-and-cover
methods. Garbage is accepted at only
eight sites. A landfill near Brisbane is
used for San Francisco's wastes. Daily
per capita refuse production is 4.4 Ib.
The present 18,290 acre ft available in
the existing sites will be fully utilized
by 1978. Tabular data is given on urban
area population, collector, fee, disposal
site, average haul, type of refuse,
vehicles used, landfill type, estimated
annual refuse tonnage, available land,
and site capacities.
65-0693
Association of Bay Area Governments. Santa
Clara County. In Bay area regional
planning program disposal needs
study-supplemental report. Berkeley,
Calif. July 1965. p.84-98.
A county permit is required of all collectors
within Santa Clara County. Thirteen
companies collect refuse. City refuse is
collected by private companies. Residential
refuse collection is provided weekly at
a fee ranging from $0.95 to $1.80 per
month. There are sixteen disposal sites,
six of which do not accept garbage. The
regular disposal sites utilize the
sanitary landfill (cut-and-cover or
fill-and-cover) methods of disposal.
Average haul distance to a site is
8.5 miles. Ten sites are privately
owned, and four others are privately
operated. Salvaging is practiced at
some sites. Daily per capita refuse
production is 3.3 Ib. This figure does
not take cannery or agricultural wastes
into account. The 19,160 acre ft now
available in existing sites will be
fully utilized by 1979. Tabular data is
included on: urban area population,
collectors, fees, disposal sites,
haul distance, refuse types, vehicles
used, refuse tonnage, disposal area
remaining, capacity and life of
landfills and projected solid waste
production.
65-0694
Association of Bay Area Governments.
Solano County. In Bay area regional
planning program disposal needs study-
supplemental report. Berkeley, Calif.
July 1965. p.9 J-108.
A county ordinance provides for:
issuance of permits to collectors and
disposal site operators, minimum of
weekly pickup, mandatory subscription
to collection service, and refuse disposal
by sanitary landfill only. There are
seven private collection agencies in
Solano County. Only the city of Dixon
operates a municipal collection service.
The basic residential monthly fee is
either $1.25 or $1.50. There are disposal
sites, all of which are landfills,
utilizing the cut-and-cover or fill-
and cover methods. Per capita refuse
production which is disposed in county
sites is 1.8 Ib per day. Adding cannery
and agricultural wastes plus sewage
sludge increases the per capita production
to 4.7 Ib per day. Between 1963 and
2000, a refuse volume of 8,650,000 tons
or 12,600 acre ft of refuse will be produced.
175
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Management of Solid Waste Systems
There are only 1000 acre ft of existing
disposal volume. Tabular data is
included on refuse collection, fees,
haul distance, type of refuse, disposal
sites, vehicles used, refuse
tonnage, and type of landfill for the various
urban areas. Charts show capacity of
sites and projected solid wastes
production.
65-0695
Association of Bay Area Governments.
Sonoma County. In Bay area regional
planning program disposal needs
study-supplemental report. Berkeley,
Calif. July 1965. p.109-118.
Sonoma Ccunty is served by nine private
collection agencies who charge fees
ranging from $.75 to $1.50 per month.
Residential refuse is collected weekly.
There are eight disposal sites, seven
of which are county-operated. Three
sites utilize a cut-and-cover operation
in conjunction with burning. The other
five are open dumps with burning.
Average one-way haul distance is 9 miles.
Refuse disposal at the sites averaged
3.9 Ib per capita per day in 1963. The
1250 acre ft in the existing sites is
sufficient to last to the year 1970. More
detailed data on collection, fees, haul
distance, disposal site and vehicles
used is given in tabular form. Information
is included on capacity of existing sites
and projected solid waste production.
65-0696
Be alert for changes to increase
efficiency. Refuse Removal Journal,
8(10):22, Oct. 1965.
The need for refuse executives to
periodically check their business or
department to reveal unnoticed and
significant changes in service needs is
emphasized. Key factors controlling
operating costs, such as scope of
service, material collected, collection
frequency, collection point, collection
regularity, population density, storage
requirements, disposal method, disposal
point distance, labor situation, and
climate and terrain are reviewed. Systems
analysis to stimulate progress, as well
as more research, including consistent
knowledge of refuse volume and seasonal
variations, a nationwide development of
uniform standards of measurement and
analysis, and uniform cost accounting
practices to aid in evaluation and
comparison are urged.
65-0697
Beckman, IM. Local versus areawide
public works services. In American
Public Works Association Yearbook, 1965.
Chicago, American Public Works
Association. p.327-335.
The Advisory Commission on Intergovernmental
Relations undertook a study to find
out which specific urban functions
are most appropriately performed on an
areawide basis and which might be better
performed by individual local governments.
The Commission's report, 'Performance of
Urban Functions' describes each of 15
major urban services provided by
government and some of the major
considerations involved in administering
them effectively. Water and sewage service
can be provided at a lower unit cost
on an areawide basis. There is some
spillover of cost from refuse disposal,
most commonly where cities dispose of
their refuse outside their boundaries
and provide proper operation of the
disposal site. Economics accrue in
operation of dumps and in refuse pickup,
but the latter economies are limited by
the increased cost of hauling refuse longer
distances, although transfer stations
modify the limitations. The economy of
having a few large incinerators
instead of many small ones, and the desire of
residential suburbs to exclude community
incinerators, make it desirable to enlarge
the administrative area for the refuse
disposal function.
65-0698
Beyond the parish pump. Public Cleansing,
55(12):672-673, Dec. 1965.
Progress of the North East British
Cleansing Institute in organizing
regional planning committees is reported.
How labor shortages are aiding efficiency,
development, and equipment use are explained.
650699
Bremser, L. W., H. T. Merwin, and P. M.
Reid. Planning (Panel). In Proceedings;
Technical and Planning Aspects of Solid
Wastes, Columbus, Sept. 1965. Ohio
Department of Health, p.0-1 to 0-13.
176
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Ub95-0701
'he background of the planning commission
.s traced, and a study conducted to
>olve the problem of sanitary landfill
sites is discussed. Studies on economics,
copulation, inventories on transportation,
lend uses and other areas necessary for
developing a comprehensive plan for the
region were conducted. Elements of the
study include: determination of the
source and quantity of all refuse
produced in Franklin County, Ohio;
investigation of present collection,
geographical load sources and disposal
methods and vehicles; estimation of
county population growth for the next
20 years; estimation of the future refuse
production of each load center; tabulation
of the present and future average daily
refuse tonnage produced by each load
center; investigation of possible
landfill sites, determination of the
number, size, and location of disposal
plants for a county operated solid waste
disposal program, and estimation of the
capital investment required and the
owning and operating cost of this county
operated disposal plant. The latter
was part of phase one to be completed in
6 months. Phase two will require a
maximum of 12 months and will include:
the preparation of specifications and
general layout drawing on long term
delivery items; such as incineratoa
assisting the Board in soliciting bids;
and the preparation of detailed working
drawings and specifications for disposal
system facilities. Phase three, to take
21 months, will provide construction
supervision in getting the program
underway. Necessary facts in master
plans include: the quality, character,
and location of the origin of solid wastes
in the community, character of the
population, and character of commerce
of manufacturing. Other points of
consideration are the reuse of sanitary
landfill areas for recreation, for open
space, etc.
65-0700
California waste management study--a
report to the State of California
Department of Public Health. Azusa,
Calif. Aerojet-General Corporation,
Aug. 1965. 411 p.
California's waste disposal problem
adversely affects its environment, health,
and economic development. No single
organization deals with this increasingly
complex problem. The Study's purposes
are to enable the state to: project and
consider the future; define waste
management's major elements; determine
the feasibility of system analysis
and engineering; and establish studies,
research, and developmental activities.
It concerns itself with output (environment
desired) rather than disposal of inputs
(waste). Waste management handling
and prevention is focused upon. Boundaries
of political entities are not considered;
significant airborne and liquid waste
movement areas are examined; projected
generation rates and cost estimates are
made, and utility of regional models
evaluated, and a developmental plan
formulated to delineate the sequence
of activities required in developing a
regional waste management system. The
study concluded that system analysis and
engineering must be employed to establish a
system that will be economically and
aesthetically effective besides preserving
plant, marine, animal, and mineral
resources. The following program is
recommended: obtain critical data and
specify assumptions for employing proper
environmental and socioeconomic models;
catalog relevant community objectives;
evaluate all major technical alternatives;
complete the overall analytical computer
models to represent and measure all
main actions. It was recommended that a
socioeconomic model be constructed with a
scaled operating model, using the most
promising waste handling techniques.
Initial component specifications should be
established, as well as guidelines for
subsequent research and development. A
State Coordinator should be designated to
assume the necessary planning, coordinating,
and supervisory functions. Illustrations
and data considers all aspects of the
report.
65-0701
Chapman, J. S. Epidemiology of solid
wastes. In Proceedings; Seminar on
Regional and Municipal Environmental Planning,
Dallas, Jan. 7-8, 1965. U.S. Public Health
Service, p.65-67.
The history of solid wastes as seen through
archeology and anthropology is reviewed.
Essentially wastes can be pulverized,
compacted, converted to another state,
or simply dumped. The primary and basic
law regarding solid wastes, merely
resolves itself into the fact, that the
community must finally assume its
responsibility and determine the most
appropriate solution to the problem.
177
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Management of Solid Waste Systems
65-0702
Cochran, D. M. Solid waste discussion. In
Proceedings; Seminar on Regional and
Municipal Environmental Planning, Dallas,
Jan. 7-8, 1965. U.S. Public Health Service.
p.55-59.
Due to the broad open spaces of Texas,
the problem of refuse disposal has not
been as pressing as it is in the more
populated states. The cities of Texas,
in general, provide fairly well for the
collection of refuse. However, complaints
from citizens concerning problems related
to refuse are on the increase. Some
cities are operating refuse programs by
methods which are no longer efficient
and are not in the interest of good
health. Reasons for this mismanagement
include lack of knowledge, lack of funds,
and the absence of authorities on the
subject to provide advice. A brief
review is given of some of the fundamentals
of refuse sanitation including: kind,
composition, and source of refuse; pollution
problems; aesthetics and vector control;
storage containers; collection processes;
and methods of disposal. The most
commonly used satisfactory method of
disposal, the sanitary landfill, is
discussed at length. Planning in all
aspects of municipal refuse handling
is emphasized.
65-0703
County problems. Public Cleansing, 55(12):
694-697, Dec. 1965.
A discussion of a paper on British county
refuse disposal is presented (see item
135-A). Voluntary regional!zation of
refuse disposal service would not
progress as fast as that aided by
changes in local governments and economic
pressures. Mobile mechanical methods
were proposed for rural use. A tip
attendant was feasible only at a central
tip, and this would also allow tipping
of special refuse by citizens instead of
dumping at vacant lots. Responsibility
of the refuse disposal officer to accept
all forms of refuse was emphasized.
65-0704
An editorial. Refuse Removal Journal,
8(6) :14, June 1965.
Well maintained equipment, courteous
employees, acceptable disposal operations,
and neat headquarters contribute to
good public relations and high morale
among employer and employees. Continuous
self-improvement is the capsule
requirement for projecting a good public
image.
65-0705
Editorial reflections--public relations.
Public Cleansing, 55(4):178-181 , Apr. 1965.
Several of the challenges in the solid
waste field in the modern cities are
discussed. Cooperation with planners and
architects, increased vehicular problems
in street cleaning, and obtaining
adequate finances for a less than glorious
service were all cited problems.
Increased news and feature coverage to
let the public know the achievements and
services of the sanitation departments,
as well as the now well publicized
criticisms are encouraged.
65-0706
Fleming, J. R. Environmental management
- a twentieth century public health
challenge. Canadian Journal of Public
Health, 56(1):1-6, Jan. 1965.
Scientific and technological advances
have exceeded our social, economic, and
political capacity to fully apply this
knowledge. The environmental scientist
is now facing such problems as mushrooming
cities, increasing complexity of water
problems and demands, mounting pollution
of the atmosphere, and awareness of the
need to maintain a balance of the
chemical and biological forces in our
environment. In the last ten years the
fringe area population growth, which
was six times that of the core city,
occurred in unprepared suburbs and in
crowded, poorly prepared communities.
The planning required by population
growth may be realized when it is
appreciated that every 1,000-person
increase in population will require an
additional 100,000 gal of water a day and
will produce 68,000 Ib of non-industrial
air pollutants a month, 365 million gal
of liquid wastes a year, and 750,000
Ib of refuse annually. The air, water,
food, and urban environments are reviewed
in terms of the necessity of accepting
the philosophy of compromise and
calculated risk, in which the advantages
and disadvantages are balanced, rather
178
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0702-0709
than the concept of safe or unsafe. Control
of environmental conditions to allow man's
existance is not enough; environmental
management should be directed toward the
maintenance of environments suitable for
man's needs and desires. The leadership
in the rapidly developing field of
environmental management should be a
challenge to the public health sanitarian
and others in the public health field.
65-0707
Garbage and refuse disposal authorities.
Public Works, 96 (3): 144, 146, Mar. 1965.
The incorporation of several communities
into an authority for the sole purpose
of providing facilities for the disposal
of refuse offers an excellent solution
to a difficult problem. The judicious
selection of participating members
simplifies long range planning, lowers
service costs to a minimum, and
allows cities to take broader collective
action. Incinerator plants can be
designed to serve future needs as well as
present-day requirements. The articles
of incorporation drawn up and adopted
by the respective legislative bodies
empower the legislative bodies to levy
taxes to pay the costs to the authority. The
authority in turn can issue self-liquidating
revenue bonds, for the purpose of acquiring,
improving, enlarging or extending facilities
for the collection of garbage and refuse.
Five authorities have been established
in the Detroit Metropolitan Area since 1947.
One of these, the Southeastern Oakland
County Incinerator Authority, consisting
of fourteen communities north of the
city limits of Detroit, was created in
1951. This authority constructed a
450-ton incinerator plant in 1954 with a
subsequent increase in capacity to 600
tons in 1964. The formation of this
authority and the legal, engineering, and
economic studies necessary to bring about
this joint community effort for garbage
and refuse disposal are discussed.
65-0708
Garrett, R. Refuse reflections. Public
Works, 96(10) : 79 , Oct. 1965.
The problem of refuse disposal is one that
crosses city, county, and state boundaries.
As our population expands, the condition
becomes more acute. There is a definite
need for a central group of experts to
standardize and give direction to the
reduction and elimination of the hazards
involved in refuse disposal. Such a
committee coulc assemble complete
information on all the methods of refuse
disposal in use, make a thorough analysis
and evaluation of each and then issue
specific recommendations. The emphasis
should be placed on determining the
best means available for refuse disposal
and research should be developed to
find new and better methods. At present,
a community has these alternatives for
refuse disposal: controlled, open-burning
dumps; sanitary landfills; composting
facilities; or incineration plants.
Selecting one or a combination of these
methods poses a formidable problem to
local officials as they need a recognized
central source of information to assist
them. The refuse disposal problem is
directly related to increasing population,
higher living standards and the trend
toward total packaging of all consumer
products. As the volume of solid wastes
will continue to grow, sound solutions for
handling them are needed.
65-0709
Gilbertson, W. E. Solid waste discussion.
In Proceedings; Seminar on Regional and
Municipal Environmental Planning, Dallas,
Jan. 7-8, 1965. U.S. Public Health Service.
p.51-54.
Close to one-half of the total amount
spent for solid waste handling, treating,
and disposal, actually is expended through
private enterprise. It is estimated that
the annual expenditure in the private
sanitation industry is over $1.3
billion. The reason is that a large
part of this private enterprise aspect
relates to industrial operation. In Texas,
large amounts of solid waste are generated
by the stock and animal feeding yards,
poultry dressing, and food processing
plants. Although this private enterprise
is something like a public utility, none
of the standards of performance or
guarantees of continuity of service
surround this field. Other problems
involve public relations with regard to
location of sanitary landfills, incinerators,
and transfer stations as well as routing
of collection vehicles through residential
areas. It is emphasized that more
attention should be given to solid
waste problems by the professions,
and local, State, and federal governments.
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65-0710
Hessing, F,. Refuse and waste disposal
and regional planning. In Refuse and
waste disposal. Berlin, Druckhaus
Lichterfeld GmbH, 1964.
The relation between regional planning
and disposal of solid waste is considered
from the angle of planning legislation.
Irrespective of whether regional planning
policy is applied on the federal, State
or municipal level, it must not and
cannot be expected to deal with waste
disposal. In describing the position of
waste disposal in the present regional
condition, conflicts are mainly due to:
the land requirements for waste disposal,
the waste disposal arrangements serving
individual municipalities. The regional
planning legislation in its importance
for waste disposal must be presented at
the federal level, the State level, the
district level, and the municipal level.
The importance of structural policy Ln
large areas is also discussed.
65-0711
Hoce, M. Solid wastes and tomorrow. In
Proceedings; Technical and Planning
Aspects of Solid Wastes, Columbus, Sept.
1965. Ohic Department of Health.
p.Y-1 to Y-10.
Developments in the field of solid waste
are traced. Federal assistance will be
forthcoming and President Johnson specifically
recommended a program of technical
assistance to the states and a program
of research and demonstration. Innovations
are being made in some areas but little
progress in others. The waste production
in the United States is increasing on a
per capita basis at the rate of k
percent per year. Estimates are made
of waste production for the San
Francisco Bay area and for Chicago.
Solid waste disposal activities in the
United States cost $3 billion per year,
or a per capita charge of $15 for each
man, woman, and child in the United
States. The problem is one of lethargy.
Although modern building materials are
available to rehabilitate slums, nothing
has been done about solid waste disposal.
Professional manpower is needed. The
path of the Solid Waste Act through
Congress with its revisions is described.
This act provides a national program of
research and development, including the
conservation of resources and the utilization
of potential resources in solid waste,
with technical and financial
assistance to states, to local governments,
and to interstate agencies. Section 203
defines the Department of Interior as
the federal agency concerned with the
problems of solid waste generated in
connection with the extraction and
processing of minerals and fossil fuels.
Section 204 provides for support of
research, demonstration, and training.
Section 205 relates to the problems of
interstate and regional cooperation, and to
state and interstate planning grants.
This bill authorizes $7 million for the
first year, $14 million for the second, and
for the third and fourth years, $19 and
20 million, respectively.
65-0712
James, J. A. Financial aspects of refuse
programs. In Proceedings; Technical and
Planning Aspects of Solid Wastes,
Columbus, Sept. 1965. Ohio Department
of Health, p.S-2 to S-14.
Fiscal planning is concerned with the
means or money to finance a governmental
operation such as solid waste collection
and disposal. Expenditure planning or
programming is concerned with the
development, execution and appraisal
of the operation. Revenue and
expenditure planning and programming for
refuse activities have common
characteristics of: a direct effect
upon other municipal programs continuous
operations; communication not only internally
but externally to the various publics
and jurisdictions, and law. A legal
basis in the area of revenue should be
found. Criteria for determining an
equitable tax or a good revenue source
should relate to a value system and
include: administration, yield, and
concepts o* equity. Characteristics of
local government revenue source should
relate to a value system and include:
taxes or levies which are regressive in
nature or at best proportional, exclusion
or exemption of certain classes of taxpayers
or properties from the levy, the fear
of citizen resistance to any new revenue
measure, and reliance upon service fees
and charges to finance local expenditure
programs. More and more jurisdictions
are developing heterogeneous tax structures.
Means for financing solid waste collection and
disposal include: general taxation and
user charges. The levy on real property
is still the backbone of local tax
programs. The administration of the real
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0710-0715
property tax involves assessment,
collection, and enforcement. Tax exemptions,
exclusions, and rate limitations also
exist for non-property taxes. The use
of fees and charges raises the problem
of whether the service confers a benefit
on all members of the community, and
whether the service should be subsidized.
The policy issues of municipal indebtedness
are lasted.
650713
Johnston, P. County problems. Public
Cleansing, 55 (11):652-657, Nov. 1965.
Problems involved in British county and
rural refuse disposal services are
discussed. Administration is generally by
an officer with other responsibilities and
would be improved if a specialized
cleaning officer was employed in a region
large enough to occupy his full efforts.
Regionalization would improve and
mechanize disposal services. Lack of
control, unauthorized dumping, fire,
vermin, and danger to children and workers
characterizes many small rural tip sites.
Disposal of carcasses from cats, cows,
sheep, swine, and whales requires special
procedure. Large marine carcasses must
be reported to national agencies, and
livestock carcasses inspected for disease
before disposal. Trade refuse from chicken
preparation, chicken hatcheries, and
bakeries all pose special problems, as
do special waste from farms. County refuse
disposal problems differ only in degree
from city problems.
65-0714
Master refuse planning. In Proceedings;
Technical and Planning Aspects of Solid
Wastes, Columbus, Sept. 1965. Ohio
Department of Health. p.N-1 to N-14.
A master refuse plan is a comprehensive
plan for dealing with refuse from its
source to its final disposal. It must be
based on facts developed from engineering
analysis. Generally, the refuse problem
may be classified into three phases:
collection, haul, and disposal. The
type of refuse collected has a definite
effect on the method of disposal, the
hours of collection, and the cost of
haul. The total expenditure in the
United States for refuse collection and
disposal is from two-thirds of a billion
to $2 billion annually. Accurate basic
data for planning and reliable design
criteria for refuse facilities are lacking.
A few years ago, the major portion of
refuse was waste food products or garbage,
but now, with frozen, packaged, and canned
foods and with increased use of home
garbage grinders, kitchen refuse has
become largely the package in which
foods are sold. Major factors in
collection are the frequency and scope
of service provided. Commercial refuse
is usually collected in a manner similar
to residential refuse, except that
frequency must be adjusted to suit the
need. Industrial refuse is usually
collected and disposed of by a private
contractor. The history of refuse
collection is traced. Technically,
composting is feasible but a commercially
successful operating installation in the
United States has not yet been achieved.
The population migration toward urban
areas and the consequent increased hauling
distance to disposal sites is noted.
Contract refuse operations and the role
of politics are discussed. Elements to
be considered in planning are listed.
65-0715
Mossey, E. A. Metropolitan approach to refuse
disposal. Public Cleansing, 55(5):313,
May 1965.
Reasons for the past adoption of a
regional approach to refuse disposal in
London and the surrounding areas, and the
expected results of this adoption are
described. A history of waste collection
in London from the 14th century to the
present is given. As early as 1666 the
city recognized a need for central agency
control of refuse, but the programs
attempted were unsatisfactory. In 1929
a researched recommendation for central
responsibility for refuse service was
defeated. In 1951 a Royal Commission was
created to examine local governments in
London and make recommendations. Extracts
from the Commission report concerning
refuse collection are included. The
commission found criss-crossing and
overlapping of disposal routes of
different councils, lack of coordination
of transfer points, high costs, lack of
research, and inability to concentrate
labor forces at particular times on
problem areas, such as thoroughfare
street cleaning. The formation of the
Greater London Council will replace
87 separate councils with 33 councils
all under one authority. This will
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Management of Solid Wa^te Systems
facilitate obtaining land for central
disposal, direction on land reclamation,
reduction of transport costs, and
establishment of a research center.
65-0716
Overman, S. M. Review of federal and
state legislation. In Proceedings;
Technical and Planning Aspects of Solid
Wastes, Columbus, Sept. 1965. Ohio
Department of Health. p.Q-1 to Q-9.
There is very little Federal legislation
dealing specifically with community
solid wastes. No Federal legislation
assists states in developing comprehensive
programs for handling and disposal of
solid wastes or authorizing research and
demonstration projects leading to more
effective disposal. A number of bills
have been introduced in the Federal Congress
but none has become law. One bill now
pending which has been passed by the
Senate is the 'Solid Waste Disposal Act'
Title II, S. 306, which amends the Clean
Air Act. The responsibility for the
administration of the program is vested
in the Department of Health, Education,
and Welfare, with some exceptions.
Eligibility for grants under the program
is discussed, as are specific monetary
authorizations. There is little
published about the extent of state
legislative authority to conduct state
level programs of solid waste control,
although a questionnaire by the Public
Health Service has indicated that legal
authority is based upon general
health or nuisance laws for controlling
wastes. There is a need for basic legal
authority and a legislative mandate for
the appropriate state agency to conduct
an active solid waste program.
Governmental authority in Ohio is
vested in municipalities, counties, and
townships. The various rights authorized
to a municipal corporation and to counties
in Ohio with respect to solid waste
activities are listed. The special
sanitary district is discussed.
Municipalities in most states and other
political subdivisions in some states
have authority to conduct solid waste
operations.
65-0717
Proceedings; Seminar on Regional and
Municipal Environmental Planning,
Dallas, Jan. 7-8, 1965. U.S. Public
Health Service. 107 p.
The seminar was sponsored by four
agencies: the Department of Civil
Engineering, Southern Methodist University,
the Texas State Department of Health,
Region V of the Housing and Home
Finance Agency of the Federal Government;
and Region VII of the U.S. Public Health
Service. The aim of the seminar was to
help both lay and professional people
in their individual problems of environmental
planning, through the experiences and
thoughts of experts in the areas of
housing, refuse handling, and general
planning. Another objective was to
exchange ideas and viewpoints between
city council members, planning
commission members, housing authority
officials , practicing engineers,
health officials, and all others
interested in this vital subject.
65-0718
Proceedings; Technical and Planning
Aspects of Solid Wastes, Columbus, Sept.
1965. Ohio Department of Health.
v.p.
The proper storage, collection, and
disposal of solid wastes has become of
primary significance among public health
authorities because of increased
urbanization and the steady increase
in per capita production of solid wastes.
A short course covering all aspects of
the problem, including planning,
was included to stimulate more interest
in the problems of solid wastes storage,
collection, and disposal and to present
avenues of approach and solutions to the
problem. The Public Health Service
prevailed upon the Ohio Department of
Health to undertake the preparation
and presentation of this subject area.
With the help of a Public Health Service
grant, nationally recognized authorities
in the field of solid wastes and planning
were obtained, and many participated in
panel discussions. The table of contents
includes; Definition of the Problem:
Refuse Quantities and Composition;
Storage and Collection - On-Site
Development, and Collection Techniques;
Disposal Methods - Open Dumps, Sanitary
Landfills, Incineration, and Composting;
Master Refuse Planning; Implementation
of a Program - Current Status, Review of
Legislation, Various Approaches, Financial
Aspects, Political Aspects, Role of the
Citizen, and HHFA and Enforcement; Role
of Education and Training - Academic
Education, Non-Academic Education; and
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0716-0722
Closing - Solid Waste and Tomorrow,
Current Research, and Summary.
650719
Refuse disposal study; regional planning
study no. 42. Akron, Ohio, Tri-County
Regional Planning Commission, [Oct.
1965]. 121 p.
The existing facilities in the Akron,
Ohio, regions are surveyed and the needs
through 1980 are projected. Refuse
disposal will soon become a serious
problem in many communities of
the region due to the expanding urban
populations, lack of proper disposal
facilities and the increase in per
capita refuse production. Sanitary
landfill in sites acceptable to the
communities is suggested as the answer
to the immediate problem and through
1980. The studies and data needed
for planning beyond 1980 are outlined.
The following topics are covered:
refuse quantities and characteristics,
collection of refuse, transfer operations,
refuse disposal methods, status of
refuse disposal methods, status of
refuse disposal in the tri-county region,
recommendations for future refuse
disposal, alternatives for refuse disposal,
financing alternatives for refuse
disposal. The appendices cover legal
considerations, preliminary work and
operational procedure for a proposed
sanitary landfill and survey forms.
65-0720
Regional approach the best solution.
American City, 80(5):44, May 1965.
Detroit found the best solution to refuse
problems by combining efforts of
municipalities on a region-wide basis.
Disposal facilities could be publicly
owned and operated. Combined collection of
garbage and rubbish is more economical.
Legislation is to be adopted to eliminate
open dumps in Detroit area. Sanitary
landfills are to be used whenever
possible. Incinerators are to be considered
part of the disposal program.
65-0721
Reid, P. M. Current status of
implementation of solid waste plan. In
Proceedings; Technical and Planning
Aspects of Solid Wastes, Columbus, Sept.
1965. Ohio Department of Health.
p.P-2 to P-10.
In the Detroit area local governmental
units dispose of their refuse outside
their borders, within the territory of
another governmental unit. In most of
the urban areas the collection
and disposal of solid waste is on a
make-shift basis, limiting public
health and community sanitation. The
strategy for developing and implementing
a solid waste disposal plan must be
formulated on an inter-community basis.
Public awareness and understanding are
essential. A committee of supervisors
from 5 member counties recommended that
the regional planning agency emphasize
facility planning, particularly for
garbage and rubbish. A project outline
was developed, planning for large areas
of land, and re-use of sanitary landfill
areas. The purposes of the project
were: to present a picture of the
current practices of collection of refuse;
to examine the various methods of disposal;
to formulate a plan for future disposal
which would insure the welfare of the
region, and to recommend future uses of
land. It was concluded that two methods
of solid waste disposal were feasible:
incineration in large-scale incinerators,
with disoosal of the residue ash in
sanitary landfills; and sanitary
landfills of raw refuse. Therefore, two
plans were developed for the 5-county
region. Plan I, in the core urban
area, recognizes the effectiveness of
three of the current district operations
and leaves them on their own. Plan II
adds 7 incinerators and places greater
emphasis on this refuse disposal process.
The use of a competent technical Advisory
Committee with a Policy Body and a
Citizens' Advisory Committee is recommended.
65-0722
Reid, P. M., J. Coleman, S. Overmate,
et al. Panel discussion of various
approaches. In Proceedings; Technical
and Planning Aspects of Solid Wastes,
Columbus, Sept. 1965. Ohio Department of
Health. p.R-1 to R-26.
The collection and disposal of solid
waste is an urban problem which must be
initially approached from the governmental
unit. The implementation of a long-range
disDOsal program is impeded by the lack
of concern of government officials in
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Management of Solid Waste Systems
the policy-making areas, budgetary
limitations, and public apathy.
Long-range planning must be done on
an area-wide basis and must include all the
governmental units involved. Data must
be developed and assistance from state
legislatures must be obtained.
Legislative and tax problems in Ohio
are discussed. There is some possibility
that Public Health Service and the HHFA
may initiate joint projects in solid
waste disposal planning in metropolitan
areas. The air pollution of New York
City is traced, citing trouble with
incinerators as a part of the anti-
pollution program. An ad hoc committee
was formed under the Building Research
Housing Authority to provide minirrum
standards for apartment house
incinerators. At present, there is no
legal provision for solid waste districts.
The problem of open dumps is mentioned.
The air pollution problem with gypsy
asphalt plants is cited. Milwaukee is
the only city in Wisconsin with a code
for air pollution. In Michigan a
licensing program requires garbage
to be cooked before it is fed to hogs,
and a solid waste licensing bill will
be implemented. The activities of the
Ohio Municipal League with respect to
refuse disposal plans are described. The
Public Health Service has a model
ordinance for local municipalities which
could be incorporated into a statewide
law. There is a need for disseminating
information.
65-0723
Robinson, C. M., G. Engle, and L. E.
Crane. Summary and course closing. In
Proceedings; Technical and Planning
Aspects of Solid Wastes, Columbus,
Sept. 1965. Ohio Department of
Health. p.SUM-1 to SUM-5.
Political leaders must be chosen with the
quality of living they desire in mind.
The citi2:en's approach to solid waste
is as negative as it was to sewage
disposal years ago. Control is
effected through local government and the
federal government allocates the funds.
Solid waste problems should be approached
and solved on a self-supporting utility
basis. Master planning is essential
and advisory committees are helpful.
Competent workers are needed. The question
of states certifying workers and
supervisors at solid waste facilities
is raised. Individual community problems
should be studied in detail as separate
entities. The rapidly advancing time
and changes in solid waste programming
must keep pace with the changing loads,
characteristics, changing attitudes, change's
in design, changes in equipment, and
changes in people. The solid waste
program in a nutshell consists of:
motivation, planning, design, construction,
operation, in that order. Although
foolproof incinerators and good landfills
can be designed, they cannot be operated
by incompetent personnel. There is a need
to inspire, recruit, train, and hold
personnel in solid waste organizations.
Too much attention is given to minor
aspects of the old solutions and not
enough thinking and research is focused
on entirely new concepts. There is a
lack of scientific approach to cheaper
and better methods. Public awareness must
have professional guidance. Unity and
coordination among all agencies and
groups must be attained. More
conferences and meetings at the regional
and local levels are needed.
65-0724
Rogers, P. A. San Francisco bay area
solid waste management and planning
problems. California Vector Views, 12(10):
51-54, Oct. 1965.
Details of the solid waste situation
in the 4 million population San Francisco
Bay area are delineated by the
State Public Health Department,
particularly with regard to long-range
planning projects. Approximately 33,125
areas of land will be needed to
accommodate the disposal volume up to
the year 2000. Unless preparatory
measures are expanded, most counties
in the Bay area will incur critical
disposal problems by 1979. The department
recommended to the Bay area governments
an immediate investigation of nex-/ or
alternate disposal methods, a regional
master plan for immediate additional
landfill site acquisition, investigation
into refuse transfer stations, improvement
of present operational practices, and
investigation of possible districts to
consolidate planning of disposal facilities.
650725
Rogus, C. A. Refuse quantities and
composition. In Proceedings; Technical
and Planning Aspects of Solid Wastes,
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0723-07
Columbus, Sept. 1965. Ohio Department
of Health. p.C-1 to C-22.
Solid wastes are commonly termed refuse,
which is defined as all of the solid
wastes of a community including those
semi-liquid or wet wastes whose moisture
content is insufficient to make the
material free flowing. Refuse can be
sub-classified into garbage, rubbish,
ashes, and special wastes, which are
defined. In addition to this communal
refuse are the agricultural and canning
wastes. Refuse can also be classified
by its origin: domestic, municipal,
commercial, and industrial. The
responsibility for the collection and
disposal of these wastes is not uniform
and is determined by local policy,
but there are general patterns. The
factors influencing quantities and
composition of refuse include: number
and types of industries and commercial
establishments and degree to which their
wastes are self-disposed; climate; seasons,
and income level. Tables give data
about: total refuse collected in 12 U.S.
cities, 1957 to 1958, monthly distribution
by weight of refuse disposed of in New
York City; 1939, and physical analysis of
refuse by weight, Chicago 1956 to 1958.
The most significant physical properties of
refuse are density, moisture content,
percent of combustibles, percent of
putrescibles, percent of compostables,
calorific values, percent of salvables,
and presence of over-large materials.
Special wastes include: demolition and
construction wastes, out-sized wastes,
synthetic wastes, radio-active wastes,
and incinerator flyash and ash residues.
There are notes to the table on
production, collection and disposal of
refuse.
65-0726
Rosenblum, H. The role of the citizen.
Proceedings; Technical and Planning
Aspects of Solid Wastes, Columbus, Sept.
1965. Ohio Department of Health.
p.U-2 to U-H.
The voice of the citizen in the matter
of waste disposal is usually negative:
complaints about the carelessness of
garbage and trash men, grumble about
litter in the streets, and, in groups,
protest any incinerator, dump, or
sanitary landfill in their neighborhood.
Most citizens give the problem no
thought at all or, if asked, say that
In
refuse should be placed as far as
possible from humna habitation. Ten
years ago citizens were just as apathetic
about sewage disposal plants. Active
citizens worked for better schools,
highways, and recreational facilities.
The need for such improvements was
evident and water pollution affected the
town downstream. Today citizens are
informed about the problems created by
lack of sewage treatment. They support
bond issues, press for enforcement of
existing laws, and urge passage of
stronger legislation. The voice of the
public can be positive if the public is
made aware a problem exists. Mass
media can help to inform the citizen.
Citizens advisory committees can be
useful. It is important that: (1) facts
be gotten and friends made; (2) a course
of action chosen; (3) public understanding
and support developed; and (A) public
support expressed where the power is.
Some case histories to illustrate these
are given from the author's experience.
(She is Director of the League of
Women Voters of the United States.) One
dealt with trash collection, one with a
new site for a sanitary landfill.
65-0727
Schmidt-Lamberg. Coordination of
sanitary planning for cities in
developing countries. Staedtehygiene,
16(10) :232-233, Oct. 1965.
The Sixth International Conference of
the Cities of African Countries held in
Ibadan in West Nigeria brought a number of
important resolutions. Foremost is the
general agreement to cooperate and to
coordinate the planning of urban
sanitation, not only nationwide, but
also between the individual countries.
While city cleaning is satisfactory for
the downtown areas of large cities, it is
necessary to include also the suburban
areas in the programs. It is planned to
increase the radius of the 'cleaning
efficiency" by 50 km every 5 years. There
is already a developing industry for street
cleaning equipment. Joint ventures for
the near future are pipe lines which will
transport the waste into the sea.
Presently a pilot project is being built
between Abohuta and Lagos in Nigeria.
Abandoned cars begin to be a problem
in many places. The twelve West African
countries have to deal with 12,000
auto wrecks yearly. Some cities plan to
build large incinerators. The cities of
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Management of Solid Waste Systems
Accra, Lagos, and Daressalam install grates
for 3,200 cu m of waste per day. Some 200 to
250,000 tons per year will generate
electric -aower and remote heating.
Another aspect of the problem of hygiene
in cities is the education of the
population. It is as important for
the battle against the increased flow of
waste as modern machinery and facilities.
(Text-German)
65-0728
Stead, P. M. Management of waste
disposal systems. In American Public
Works Association Yearbook, 1965. Chicago,
American Public Works Association.
p.110-114.
Although California faces crises in the
fields of air pollution control and
water resources, the problem of waste
disposal is the most acute. There has
never been a system of disposal
for municipal solid wastes. Landfill,
which is terminated when the available
space becomes exhausted, has been the
most commonly used method of disposing of
municipal solid wastes. Oxidation ponds
and lagoons have been used for removal
of unstable organic material from a wide
variety of liquid wastes. There have
been breakthroughs in the removal
of nitrogen, phosphorous, and other
nutrients. The reclamation of a high
proportion of waste waters in inland
areas is planned. The organic waste
is being converted to usable products. In
biological conversion of organic wastes
by either aerobic composting or by
anaerobic digestion, both nitrogeneous
and carbonaceous wastes must be utilized in
proper proportion. Garbage can be
combined with sewage sludge, and in
agricultural areas, animal and poultry
manures can be combined with carbonaceous
wastes to produce compost by the aerobic
process. Cellulose commodities such as
tree limbs can be converted by destructive
distillation processes into a carbon
product with gaseous by-products. By
shifting from landfill to conversion, the
end products are permanently removed and
assimilated. Thus, the keys to the
solutions of California's waste problems
consist of converting and recycling the
liquid and solid wastes and of utilizing
relatively wastefree sources of energy.
65-0729
Tri-County Regional Planning Commission.
Refuse disposal study; regional planning
study no. 42. Akron, Ohio,
[Oct. 1965]. 121 p.
The existing facilities in the Akron,
Ohio. region are surveyed and the
needs through 1980 are projected.
Refuse disposal will soon become a
serious problem in many communities of the
region due to the expanding urban
populations, lack of proper disposal
facilities, and the increase in per capita
refuse production. Sanitary Landfill in
sites acceptable to the communities is
suggested as the answer to the immediate
problem and through 1980. The studies and
data needed for planning beyond 1980 are
outlined. The following topics are
covered: refuse quantities and
characteristics, collection or refuse,
transfer operations, refuse disposal
methods, status of refuse disposal in
the tri-county region, recommendations for
future refuse disposal, alternatives for
refuse disposal, and financing alternatives
for refuse disposal. The appendices cover
legal considerations, preliminary work and
operational procedure for a proposed
sanitary Inadfill, and survey forms.
65-0730
Tucker, N. E. Definition of the problem.
In Proceedings; Technical and Planning
Aspects of Solid Wastes, Columbus,
Sept. 1965. Ohio Department of Health.
p.B-1 to B-4.
One simple cause of solid waste problems
is public apathy. The mounting garbage
and refuse piles are examples. Community
education is necessary to change open
dumps to sanitary landfills. The
responsibility for solid waste- disposal
lies with elected political officials
who traditionally avoid the issue. In
university planning departments there is
a dearth of theory and application of
principles for the collection and
disposal of solid wastes. Health departments
are often complacent. The land
available for disposal sites is diminishing
while the volume of solid wastes is
increasing because of increased population
and increased amounts per capita day.
Costs are rising because of: equipment,
maintenance, labor, land procurement,
inflationary trends, diminishing
tax funds, reluctance to increase charges,
and municipal bondability limitations.
Solutions to the problem are: increased
community education; change of political
attitude or the removal of solid wastes
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0728-0733
control to a non-political entity;
augmentation of planning curricula
to include solid wastes and/or specialized
training for practicing planners;
stimulating health departments with
adequate legislation, staffing, training;
increased research and training in
developments which result; the realization
that solid wastes problems should be
treated as a utility service to the
consumer with the payment necessary to
operate it.
65-0731
Tucker, N. E. Solid waste discussion. In
Proceedings; Seminar on Regional and
Municipal Environmental Planning, Dallas,
Jan. 7-8, 1965. U.S. Public Health
Service. p.49"50.
Of 140 million people in the United
States only 100 million receive refuse
collection service. Of 2,500 U.S. cities
which have populations over 2,500, less
than 50 percent have what is designated as
approved nuisance-free refuse disposal. The
solid waste problem is broken down into
4 segments: site storage, collection,
disposal, and planning. The three
variables in refuse handling are: vacant
land, refuse production, and population.
For sanitary landfill, which is the
most prevalent of the accepted disposal
methods, the requirement of one acre per
year per 5,000 population is applied.
This applies when the refuse is compacted
to a depth of 10 ft. With a properly
operated sanitary landfill, land can be
reclaimed for many uses. Changes in the
refuse industry have involved the use of
containerized systems of storage by
industrial and commercial establishments
and the use of the refuse train
system--a series of trailers pulled by a
pickup truck.
65-0732
Williams, K. HHFA and ordinance
enforcement. In Proceedings; Technical
and Planning Aspects of Solid Wastes,
Columbus, Sept. 1965. Ohio Department
of Health. p.V-1 to V-8.
The Housing and Home Finance Agency (HHFA),
created in 1947 to direct federal
programs in housing and community
development, operates through five
constituent agencies: Federal Housing
Administration, Public Housing Administration,
the Federal National Mortgage Association
(Fanny Mae), the Community Facilities
Administration, and the Urban Renewal
Administration. The purpose of the last
is to provide funds for comprehensive urban
planning and to give financial and
technical assistance to communities
undertaking urban renewal. Urban renewal
programs are initiated, planned, and
carried out by cities, not by the federal
government. Most of the new construction
and rehabilitation is done by private
enterprise. The open space land program
aids local or regional public bodies
acquire and save open space for
recreational use by grants covering up to
50 percent of the cost. Sanitary landfills
may be acquired under this program provided
that the sites are developed for
recreational use within 10 years.
Comprehensive plans and local self-
improvement are necessary. More than
2,400 communities have programs certified
by HHFA. These include adequate codes
that provide sound standards for new
construction and govern the use and
occupancy of all housing units. Model
codes have been developed, but local
codes are acceptable. Codes are useful
for enforcement, to prevent blight, and
as educative devices. All these programs
depend upon local citizen action. Public
hearings, project area meetings, and
involvement of those whose lives will
be affected from the start are all
important.
65-0733
Wither/spoon, J. Political aspects of
solid wastes. In Proceedings; Technical
and Planning Aspects of Solid Wastes,
Columbus, Sept. 1965. Ohio Department of
Health. p.T-2 to T-7.
Solid waste disposal is essentially a
local problem. Urbanization has erased
the traditional relationships between
city and county governments and today many
large cities are trying to hand over
to their counties those municipal services
like waste disposal which benefit all
residents of the county. The National
Association of Counties (NACO) has eleven
full-time professional staff members
and works on such projects as the Local
Official's Community Action Program in water
pollution control, air pollution control, and
solid waste disposal. (The author is
Associate Director of Research, NACO).
Growth in population is taking place in
unincorporated areas which will have to
187
image:
-------
Management of Solid Waste Systems
provide municipal type services on
a large scale with high capital
expenditures. These local jurisdictions
have had little experience in providing such
services. Cities and urban counties will
hai'e to seek other means of disposal than
the traditional means in someone else's
territory. Three local political factors are
important: politicians themselves;
charateristics of local government; and the
citizen's response to local issues. Three
general types of local politician are:
the single-minded office holder, the
non-leader, and the performer. The
first is the most dangerous. The
non-leader needs pushing. Local
government can be considered from the
points of view of authority, structure,
and age. Good citizen response to public
issues is of prime importance.
65-0734
Zehnder, E. Waste removal is a regional
problem. Brennstoff-Waerme-Kraft,
17(8) :375-378. Aug. 1965.
In industrial areas with high population
densities the removal of waste is largely
a problem of planning and organization. The
task becomes vastly more complicated if
political questions arise. This is the case
in the area of Basel, Switzerland, where
Germany, France and Switzerland
meet , the latter represented by not less
than five cantons. Despite these
difficulties, cooperation between all
parties concerned must be achieved,
since only large-scale planning
leads to both economical and truly
satisfactory solutions. Thus the large
waste incinerator of the canton Basel is
supplied by waste and chemical refuse from
communities even from across the borders.
In densely populated areas, incineration
is the preferred waste removal method,
supplemented by the deposition of slag
and ashes. Also, it is more economical
to build one large incinerator than
several small ones. Transportation costs
should not be overestimated, especially
if superhighways can be used. Large
plants cope more easily with chemical
refuse and sludges from sewage systems.
Small incinerators are advantageous only
if the transportation and heat distributior
conditions require them. Two maps show
the population densities of the area of
Basel for the year 1960 and the expected
densities for the year 2000. (Text-German)
188
image:
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ADDRESSES OF PERIODICAL PUBLICATIONS CITED
Agricultural Engineering, American Society of Agricultural Engineers,
2950 Miles Rd. St. Joseph, Mich. 49085.
Air Conditioning, Heating, and Ventilating, Industrial Press Inc.,
200 Madison Ave., New York, N.Y. 10016.
Air Engineering, Business News Publishing Co., 450 W. Fort St., Detroit,
Mich. 48226.
American City, Buttenheim Publishing Corporation, 757 Third Ave., New
York, N. Y. 10017.
American Journal of Public Health and the Nation's Health, American
Public Health Association, Inc., 1740 Broadway, New York, N.Y. 10019.
American Public Works Association Reporter, American Public Works
Association, 1313 E. 60th St., Chicago, 111. 60637.
American Public Works Association Yearbook, American Public Works
Association, 1313 E. 60th St., Chicago, 111. 60637.
Archives of Environmental Health, American Medical Association, 535 N.
Dearborn St., Chicago, 111. 60610
Brennstoff-Chemie, Verlag W. Girardet, Postfach 9, Essen, Germany
Brennstoff-Waerme-Kraft, VDI - Verlag GmbH, Postfach 1139, 4 Dusseldorf,
Germany.
Bulletin Technique de la Suisse Romande, Imprimerie la Concorde,
Terreaux 29, 1000 Lausanne, Switz.
California Vector Views, State Department of Public Health, Bureau of
Vector Control, 2151 Berkeley Way, Berkeley, California 94704.
Canadian Journal of Public Health, Canadian Public Health Association,
1255 Yorge St., Toronto, Ont., Canada.
Canadian Medical Association Journal, 150 St. George St., Toronto,
Ont., Canada.
Chemical Engineering Progress, American Institute of Chemical Engineers,
345 E. 47th St., New York 10017.
Chemie-Ingenieur-Technik, Verlag Chemie, Papellale 3, GmbH, 6940
Weinheim-Bergstr., Germany.
Civil Engineering, American Society of Civil Engineers, 345 E. 47th
St., New York, N.Y. 10017.
Combustion Publishing Co., Inc., 277 Park Ave., New York, N.Y. 10017.
Compost Journal, New Zealand Organic Compost Society, 875 Ferry Rd.
Christchurch, New Zealand.
Compost Science, Rodale Press, 33 E. Minor St., Emmaus, Pa.
18049
189
image:
-------
Addresses of .Periodical Publications Cited
Electrical World, McGraw-Hill, Inc., 330 W. 42nd St., New York, N.Y.
10036.
Engineer, Morgan Brothers Ltd., 28 Essex St., Strand, London, England.
Engineering News-Record, Fulfillment Mgr., Engineering News Record,
PO Box 430, Hightstown, N.J. 08520.
Farm Chemicals, Meister Publishing Co., 37841 Euclid Ave., Willoughby,
Ohio.
Food Engineering, Chilton Co., 56th and Chestnut Sts., Philadelphia, Pa.
19139.
Health, Education, and Welfare Indicators, Superintendent of Documents,
U.S. Government Printing Office, Washington, D.C. 20401.
Heat Engineering (Was changed to Netsu Kanri), Chuo Netsu Kanri Kyogikai,
8 Ichigaya Kawada-cho, Sinjuku-ku, Tokyo Japan.
Heating, Piping, & Air Conditioning, Van-Nostrand-Reinhold Co., Inc.,
120 Alexander St., Princeton, N.J. 08540.
Hydrocarbon Processing, Gi^lf Publishing Co. Circulation Mgr.
P.O. Box 2608 Houston, Texas 77001.
Indian & Eastern Engineer, Sohrah House, 235 Dr. D. Naorgii Rd.
Bombay, India.
Industrial Heating, National Industrial Publishing Co., 1400 Union
Trust Bldg., Pittsburgh, Pa. 15219.
International Journal of Air and Water Pollution, Pergamon Press, Headington
Hill Hall, Oxford, England.
Journal of Air Pollution Control Association, 440 Fifth Ave., Pittsburgh,
Pa. 14213
Journal of Environmental Health, National Association of Sanitarians,
Lincoln Bldg., 1550 Lincoln St., Denver, Colo. 80203.
Journal of the Institution of Public Health Engineers, Municipal Publishing
Co., Ltd., 3-4 Clement's Inn, London, England.
Journal of the Sanitary Engineering Division, American Society of Civil
Engineers, American Society of Civil Engineers, 345 E. 47th St.,
New York, N.Y. 10017.
Journal of Water Pollution Control Federation, 3900 Wisconsin Ave.,
N.W., Washington, D.C. 20016.
Modern Sanitation and Building Maintenance, Powell Magazines, Inc.,
855 Avenue of the Americas, New York, N.Y. 10001.
Paper Industry (Was changed to American Paper Industry), Paper
Industry Management Association, 2570 Devon Ave., Des Plaines, 111.
60018.
Paper Trade Journal, Lockwood Trade Journal Co., Inc., 551 Fifth Ave.,
New York, N.Y. 10017.
Plating, American Electroplaters' Society, Inc., 56 Melmore Gardens,
East Orange, N. J. 07017
190
image:
-------
Addresses of .Periodical Publications Cited
Public Cleansing, The Institute of Public Cleansing, 28 Portland Place,
London, England.
Public Health Inspector, (Was changed to Environmental Health),
Association of Public Health Inspectors, 19 Grosvenor Place,
London SW1, England
Public Works, Public Works Journal Corporation, 200 S. Broad St.,
Ridgewood, N.J. 07450.
Refuse Removal Journal, (Was changed to Solid Waste Management:
Refuse Removal Journal), RRJ Publishing Corporation, 150 E. 52nd St.,
New York, N.J. 10022.
Research and Industrv, Publications and Information Directorate, Council
of Scientific and Industrial Research, Hillside Rd., New Delhi, India.
Schweizerische Bauzeitung, Zuerich-Giesshuebel, Staffelstr 12, 8021
Zurich, Switzerland.
Staedtehygiene, Nuer Hygiene-Verlag in Medizinisch-Literaris Chen
Verlag, Dr. Blume and Co. Ringstr 4, 3110 Uelzen, Germany.
Surveyor and Municipal and County Engineer, (Was changed to Surveyor and
Municipal Engineer) 40 Bowling Green Lane, London E. C. 1, England.
Tappi, Technical Association of the Pulp and Paper Industry, 360
Lexington Ave., New York, N.Y. 10017.
Tonindustrie-Zeitung und Keramische Rundschau, Herman Huebener Verlag KG,
Postfach 68, 3380 Goslar, Germany.
The Wall Street Journal, Dow Jones and Co., 44 Broad St., New York, N. Y.
Wasser und Abwasser, Gas und Wasserfach (GWF), Rosenheimer Str. 145,
Munich 8, Germany.
Waste Trade World and Iron and Steel Scrap Review, McLaren and Sons,
Ltd., Davis House, 69-77 High St., Croydon, Surrey, England.
Water and Sewage Works, Scranton Publishing Co., Inc., 35 E. Wacker
Dr., Chicago, 111. 60601.
Water and Waste Treatment, Dale Reynolds & Co., Ltd., Craven House,
121 Kingsway, London, England.
Water Works and Wastes Engineering, (Was changed to Water and
Wastes Engineering), Rueben H. Donnelley, Corp., 4 Lexington Ave.,
New York, N.Y. 10017.
Western City, League of California Cities, 702 Statler Center, Los
Angeles, Calif. 90017.
19t
image:
-------
192
image:
-------
AUTHOR INDEX
'•i.i,[ TbO'li O.L. BuACK, r.J.
,., L i i'u, ",.[<. hLOIJKt n.M.r.T.
b'/.-:u,u'J 65-02b2» f
«!.uliMAN» J. ,. o5-0?.6ti» 65-026or 6b-u267,
/. of F f • L) , f- »J •
» '',0 K, j.
oS-<"4U' 6. CK LYi.i , u.i'. 6S-033t_,i
i.'" Ll_Ai- ilJ4 BUTOAR, S.L.
H t, ';,'JU» rv. 6r>-0177
o'>-^44.-5 f3«rlOt 'jf'ACH, A.W.
n'Yb, L. '. 6S—0423t 65—Ob3i»
, ' CM T7 » J.L.
A Ci.i ANr u.
bb-; n'^7 65-026°
t>t I U. » K./. f'KONSOrj » J . C •
LLr C. . bUNCH, R.L.
L.L. J... ' BURRAriK' N.C.
bb-0')'42 bb-0487
; i JvJi.S, H.H.
b'3-U207 i,! J(,/'\/AOI"» J.vi
• _iNi,, iJ. ijb- 4 ,•:••>
b'.j-li', 17 i;i bT, MLiJ , t i '<• .
bb- . 1 7j
LivOt.i:* d. .M LI > J.i .
6b-0213 0 ,_ ;. / L
'n' H . C . t. j l '_>, j.
IIMOP, W.D. c L.Lon, » . ..
6S-0587 t/_;_ ,(1)<,
193
image:
-------
Author Index
DAVIS, ''.
U ,. > iC,.At L, v .
i, . J » I\.L. IJLASY, c.^i.
i^.'rTt K, ,i.P. DhNl'jOM H.I.
o'j-t.'O'j 65-Oo2;>
I-I.I-, I I '<, (' .(. . t.Juf" , I5.1!'.'.
6b-, l.'^7 o5-044"
oS-0?Ul 65-0109, 65-ul^o,
i_i'Airf:t, -. 6')-01'32, 65-0195,
ob-i!.Ml, 65-OUi^, L.5-Oo4" UOMMULr J.!\.
L A •-: F.5, - . 65-0275
u ii ,LKA, j.j, 65—0014
o >-!..-"ii DoYLE, F.S.
(-L AY , J. o5-04Hl
, L.I .
4Y, U.L.
Du'XA, J.6.
i.' - i ,,i , UUCK ,,(;i:TH, S.
f.'i- 'ioi DUDLEY, c.j.
,/_,- '.$>_ do ;KLI:S, K.
L U, ,»<-,..• t)' j — u 13 7
bki-'''-t _>1 Ck,1'!'">TA| i» o.h,
i. L L . Y , . L .
C v.i(
'! I., .C. , r ML , i- . ,.
i 5- Mi j t/-,-'U 7,,
'' : • • i « 11 YV.I-, , A . .
o5-0o'4t u1,-' 14 i
;"Y, P.O. e- bliKLl •, O.L;.
65-0^3>) oS-'.jH-i
I G , r.. ,;. i Y , ;;. o .
C:-;" 'JL r I .t . l i. KL » Li. .
CK'' .Till :', 0. i .-(j'.D'.t O.L •
CULOTT,'-, o.*-. Li.,i',bv->, ^.L.
CU'JOY, L . L .-,; : Lib, I'.K.
bb-OH?', 65- t,!>r>
H.i . r-' LLrbr V.M.
13:', 65-bu?l tJ'.-i ,,3
.':,, A.G. L- ";'f L'X'L' l..i .
tj5-0i,4;i, 65-l:lcl,,, ^,,-0^74 b''~ In'/, t)'_>~G 1'-0» o5-01''l,
DAVILC,, A.J. ' o5-..l", , o5-01Vi, 05-0194,
194
image:
-------
Author Index
L I, L I S > r I . M .
ob-0 19b
Li oLi » u.
65-0723
LI GLI5H. M.C.
65-0^77
LI Hlo» T.C.
6b-00i4
LI-HAuL). H.
6b-019t.
Li.YTt-HoP L» h.
65-flb49
tlTLlJf 0.
6b-0b23
L1TIuGtK» M.f.
ob-'J4^H
LvAliS. H.
6'>-i]<44o
Fr.lRLH. • P.O.
6b-i
h AIO^ ASijI f G.
bD-Or'-TlS
FAKt..,LL» J.
bt,-OJi'l
^ t Ki r( f ! '.
t>S-f)'!ftn»
FINSTFIN. M.r3.
GLOn>6E. J.C.
65-0092
65-Uo7e, 65-037'}
65-0037
FLEFTkv'OOD* J.E.
65-0089
FLEMIfJG' J.H.
65-070,
FLIEGLR' K.
6b-0022
FLOOn» L.P.
65-0341
FLOWLKf W.A.
65-0446
FOLLETTf R.H.
FOX. E.C.
65-0178
FULLER. »l. H.
65-0279
FUSS. K.
65-0485
FUSSELL. O.P.
65-0550
GARDNER' J.C.
65-0036. 65-0037
GA.r?NEH» J.F.
65-0016
GAPRCTT. H.
65-0198. 65-U70.J
GA^KELL. J.
65-0091
GAUDY. A.F.
65-0466
6b-0709
GiTCHEL. rt.B.
65-0450
GLYSSOIJ. E.A.
65-063'i
GOODEVE. C.F.
65-0551.
GOOOMAN. B.L.
65-044;'
GOODROW. T.tJ.
6';,-059b
GKfOj. L.B.
W.F.
6b-03?l
65-0449.
j. G.f.
65-0454
GKOSS. A.T.
65-.,. bl
o. uE ..AL , A.
t3b-;i'(rju
A . I .
Ob— > ! ,5':) J
fi; i-iSO t . C >
L)5-"'.Jl.'
Ki TT> J.
r- f . I'
LL .
..Alif., H. .
b5 — us b^1
. i; MU,. . 'j.H.
65- -41^. 65-0455
i!A,'(,INO. J.C.
1 1/,,. T F b. ' .
ub-'Jl'J-J.
M. u .Oil . T.
65-0340
Ml j'.,lNG » F .
fab-071u
M TLjtJO. L.J.
b 5 — 0 *+ b a
Mr ^L L EK IA!.» M.
Hl;Jt Ji. t .
195
image:
-------
Author Index
I i /-. IV f I-
t, •_>->! 71 j.
i u..i'i i i« • C •
.!• bf L ' u.
Dtx-'-t/J';)
I II J j'^Uf • J.
bb
Ml Li'i'LL
lUGWf RSrU» 11. H.
hS-Ojys
lKVIItb» C.~.
b'.-0^'4(,
J^COlU* J.v«.
0b
A.
n.
bb-0
JA'U'Sr J.A.
b^-oyu
JLMt:ijCI<» T.I-'.
bb-O^Oo
Jh MSF rj , C . L .
G'l-OUbU
JOHNSOIi' L.f,.
JOHNS TON » P.
6c,-07l;3
JOfJL'Cf P.M.
JORGE MSF."N» P.J.
br,-01<+lt
JOYftf R.b.
6 5
W.
i09
kACHULLL'f C.
b')-OJ8b
KAMPLHT' A.
6b-014'^
KAMPSCh'JLTLf J.
6b-03rt7
KA^I^RA^ G.A.
KAPLANr K.
b'j-006?
6'j-020.i
65-009b, 6S-020-4
F.K.
KLFGAN, P.
KtLLt K. E.G.
bS-0479
KL'IPLr L.L.
6. -' l'4o
M.I. T ri i< • it.
D'.l — 1.., 15 I
r',, nl I i O , . .
t j S — ' i ^ o 7
i\i OLL • i ' .
U..~ .?>.'!()
iv UPl » H.V.
t)1)— 'Hj.'i
i'.i 'C',.1 LI f ,f .1. •
t;S- .,97
h, .. C i ' f "• . .
i>s-0,.0,.
r\-Cl. I I I/KY» C .W.
fa:j-031 J
i-.v U/ "L» ;-'.
b',-01'* /
K, A1 • !<• K'.tt.
b'j-Ubl i
M. r\ /n • ' I . J .
o'.- ,.|7i
M .v At A I • J. j.
o'i— ^i,''>
f I'll 'I ' VI.
rVj-. "O'^r bb-0.
(\ . i j i : o i o i r .
bL> — f i. u 1
u; _,,. Gl r f .
b j-1, i,6i
ui I' • F" .
u - 1 4 i
L,i •-[ .<(j» O.'j.
u ,- V*-i i
u . u._ ' Tt i .
b1..- \ ,,o
u.i
L . Vi t.Y. i. .
196
image:
-------
Author Index
L . J r > u « L> «
to- It-'-f,
LOFTHKr P.C.
fa'j-0471
IG, H.F.
Lul.FYr H.J.
6S-0<+7.
LUTIN. P. A.
Ofi » b.L.
MAAC, » K
blv
MAC Kt[!7It» y>.G
VAC LEOH. j.c.
bb-OblO
M.N.
bb-0477
O.v, >
'/Mr,HNI, C.I.
bb-Obbt,
MATTOHIf R.ii.
bb-OH79
'•lATUbKYr K.t .
b'j-04^0
i-'AYSTi.,-0474
yC DOfJALOr J.P.
or,-01'«"
:-'.C KiNLTY. J.i .
KIl.'jfY, i'.t.
f,';-020 7
LF.IO«EF L.
u', -U2B4
'.-MI.^TLKr J.K.
bb-0"»7i
"Cl i( • ki . A .
oS-04ol
'-M'J. H.T.
o',-0o9c'
CiHALLSf A.
bb-03Sl
DilLE- TOOK'.,, F_ ., .
i 'v Oi' ' AiJ i K .
t>b-f ^j't
•.I r(^AN» J.".
nb-^Uo?
. .' LC I'LLL » ix . t,
ob-U.i^o
( ' o i! Y » f . * .
fc>S-'.71-j
. • L LLLt -i'K,r
b'j-iiSb'Jt
i ' t J l K » 1 • . , .
ub- H71J
. . i. - I I / • ,- .
6b- >Ho4 '
i .1 X t M.L.
.1 v iv.» ' .
O^-Oobi
u :.! AUV» i .
tjb- iHlJ /
' KL- Y , i .!{.
r>r.-ii..bti
',_i,i IJL UL » A.I,
oS-l -,b "i
* >_L, K T r C . J.
o L — H :j 1
T . K • r .
6!>-Ojr>
. t A . , r ' , . N •
b' -.' ,'lt;
*A I I ' i» « . J.
u,- — • ' i ;,.
i I ,Ui ',) f > o.i,.
bb-o I 'Ji » i) j-0,, j7
IJ » M.H.
6b-0;>oC
PATE •'OMF.U. A.C.
bS-Ol'j?
P/,'.'r l.K A» fJ.K .
GS-OJ3b
PL^LSTF.in. J.
r,')-ObtV>
PS P'n.TK'!» R.
6r,-0j93
Pt YSLI'r II.
6l'-0u3t,
-, r J.I.
197
image:
-------
Author Index
B.V.
65-0491
P1MGLON* tl.
65-0158
PIPE'S, W.O.
bb-049;: , b5-u49,,
PULLOCK, C.L.
POLONCSIK, S.
bb-0493
POOLE. N.D.
bb-032b
POGTOiJ, H.W.
t>5-0494
PRATT, L.C.
(,'.,-0630
PbRCELL* L.I.
S.R.
6C>-060> , 65-060 i, ,-OblO,
65-0611 , 65-061.-
QUTL.LF.fi* B.C.
bb-035°
QUOM, J.ET.
6b-Ol6U» 65-049-,, bb-049'.)
kAHB, A.
65-ObOi,
RASCH. S.
RLf.VFS. J.il.
6',-02a9
r F.R.
65-036;?
. r-.M.
6'_>-069->, 65-U721* bb-072?
6b-0b01
RLY'JOLLiS* J./\.
RICH, L.G.
6^-0213
K i v.KL I- S » i\ . M.
ijS-.lr' 14
»- i Li !. I'lUr"!1 » K . A .
ob-'i 3«ju
l< Il_t 'l • (V .11.
o'j- t)J2» 6S
hi i i, r.oi-j» c . K.
L> 'i — ' 1 1 1 f.
!<• C.!. t_l' • • . F .
6b- 113
K, ij; l r I-' . A .
uuu', » L . <" .
ob-r3jl»
< MLICii* C« A •
6b-0i.kt;
.US( V/LLTr J.
iLi.» A.,'..
6L-',47u
IM/J'J! LL* H.R.
6'j-0b27
LJI bLi- ' J. C .
6S-U304
'j//-',-,A* A. A.
oS-On^U
jf" 1'Ji.i, R j r K . F .
tj')-o:'t>9
.j/nr^Kb'* C.F.
KG
,- 727
kr F.
j-n ,7o
bb-0137
SLHWttLEK* U.T.
bb-0490
StIDEL, H.
bb-ObOb
SHAPIRO* M.A.
65-04 10
SriflYNF. P.E.
bb-033?
SHEAHAfJ* J.P.
b5-0b07
SiiEPPARP, P.f.
J.M.
b5-ObO»
SHFRRILLr C.A.
bb-0632
SriULTS, F.
bb-02bO. br)-025l
ShULTbr f-.S.
b5-021b
SHUMATE, K.S.
bb-0413
SHUVAL, H.I.
b5-004n
, L'.K.
65-0509
198
image:
-------
Author Index
SMITH, L.L.
65-0510
SMITH* P.M.
65-0511
SwITHr R.
SMITH* W.H.
&5-057
SOHR, -,v«H.
65-0512
SOMFRVILLE, A.T.
65-025.3
SHEER, R.D.
65-0567
SPOHN* r.
65-029 ,
STEAD, F.i4.
65-072;
STEEL), H.C.
65-0649
STFEL* T.W.
65-008,3
STEIN* J.
65-OD13
STEPHENSON, J.w.
65-0514
STFRLlNGr M.
65-0368
65-063.)
t K • t- •
65-0574
bTiHi-UP* F.L.
65-1*115, 65-0116, 65-0163,
6b-Oj9«J, 65-0575,
6'j — uol l>
bTuKYr W.S.
'jlOVALL* J.h.
6b-UJ
H.
STt\0',b* R.O.
ob-l.blb
K» V.A.
65-0099,
.
6b-0o3b
L.P.
R.S.
T.A.
R.
F/.OltK* F.
65-0 lit,
Tf YLuR* L.tl.
65-0332
1A1LOK* R.C.
ob-0 16 j
It t.f<(.VA* h.
6', -0302
T- LLlZKL, G.h.
fab-C^Sb* 65-0517
Tr.Uhi AfJU
ob-C'577
li ui(tit3Ui <•' vj 5
Tl-^M, H , .1. .
t,5- 7^9, 65-0730
ruivu; K , d .ii>
' i_ L "
, o • A .
A > M . f-'i •
VlLLtMONTE, J.R.
65-0 52,>
VlRARAGHAVAfj, T.
65-052i;
VI5SLK, S.A.
65-0305
VOGfL, H.c..
55-0227
WALKLH, J.F.
65-0521
WALLACE, A.T.
65-052?
WALTERS, W.I .
65-0523
WALTON, 6.
65-011'.)
VtANGtKI'J* D.D.
65-0371
WARD, G.LJ.
65-049^
WASMKJOTOtJ* j.R.
WATSON, KtS.
65-033?
WEAVER, L.
65-053o
WERRER, P.
65-0343
riLINHURGH, H.B.
65-030u, 6S-u30/,
65-U30M, 65-U31J, 65-0311,
65-0312
ALl-Jj, A.J.
65-058t,
WLLLER* L.v:.
65-037;
199
image:
-------
Author Index
WENZLi H.F.
65-0525. 65-058^
S.J.
65-0160
WLSTONr R.F.
65-0220
WHITE. K.E.
65-0051. 65-U05.;
WIEHLE. C.K.
6L>-0082
J.S.
65-0121. 65-031 _,
WILKlMbONr H.
65-0255
WILLIAMS* K.
65-0731
WILLIFORD* U.K.
T.£.
0373
C.P.
r I-'.
fa?i-CJ«*Oo
» Ct
.»' OtJLANU» K.G,
ob-0bc7
K.A.
C.
K.C. ,
6b-'Jt.36
65-0*107
Ai-LTht image:
-------
CORPORATE AUTHOR INDEX
AI,< Puu ul ICM CONTROL ^SbOClATIOu. !!ES, YCRK
u-
AiML ;ICA,, F\UL1C <«Of-KS ASSOC.r CHICAGO* ILL.
o'_.-0103» 65-C10<4> 05-062^., o5-ObBO,
bS-i.:,i97
RK/MJI^S S,ATE r>LHT. OF HL.AUH
o-)-wijbl
bb; ci/.n-j . uf- LAY AREIA uOv'eR,,!;:,,,Tb. ^ERKLL?Y> CALIF
t>';-^u-'j£:2ti> 6o-0?76' ob-0j28» oS-0^95
^.,i »C-SCiti\C" - IflC.f A«CAOIA» CALIF.
ot.-CL>9'4-
^ ST!>Tt , C/mD OF HtALTH, TALLAHASSEE..
.. .-0107
s L-Li T. ,vF r'LiiLIC i-iiiALl'Hf AlLAnTAr GA,
6 i-doOe
OF HUL5LIC CLE/.,,SIJu. LOuiJO!-i
ob-fj,l<-'» o5-030d» 6b-046rJ» b
bb-Cfcb?
f:ATIO.,AL At.ACt£"Y ^F SClEuCti5. :,ATlO;'Ai_ RESfL/ PCH COUNCIL. «AS>iINGT&N
6' -.'-^OC
I.Ai:0,.;.L A' 'UC'JLTO^AL CHL.-1IC»LS rtbSCC 1 AT 10' j r W,'.SHIMGTOn . O.C.
DA'vAL Civl,. LU(-Ir;Lt:.RU G LA....f PORT HUtNCHt! r CALIFORNIA
b[ — Jlfcl3
kOh TH C'«OiIt,A STATE U']I\/t.:;Sil Yf r<,\LEiGH, ;.C.
bs — ( fi5H> b5— ,^
01.10 b'l/TL UtPAf.Tiv,ri4T OF itf:ALT"i C'"JLU:-i:iUS.
65-0 71fi» b5
b'lATt U .IVL-.SIIY t-Iv,.IULl:'-(Ii4-' EiXPF RL'F "i'T STATIONr CORvALLIS
oc. — i'33o
. TV, 5C.T..CF AuVIbOrtY cr :.',,-ii TTLi£ , dASMlN-jTOiJf D.C
oS-023(i>
201
image:
-------
Corporate Author Index
(• UoLlt ! • c.ALT'-! 't- ;
<.- — ".bi>0» bts — '.'701
Put.; ut . ,avrj;STn. LAr
o',, — r' '_-17 t C'j— •- ~j?-'{-
. b , -MCifAL l_F.'(JUr» ^OSTi,., Tt-^'S
o Li - 1 j. 1 «J
-Ct^i , , iFGTl'u/.L PL"inI,,f, CL ulSSIOj. ,',.. Q.J, OnIO
<_ -. ?1V
Co i' ^- TJ.O » ,:,i.i LI; c)/,,-,c » C' LII- iirt.i A.
LO Il-M^ri U V;,,^l/( 1 IGf.. ;,,,.! jTu A • .j"iT2'r; 'ivtl
202
image:
-------
GEOGRAPHICAL LOCATION INDEX
AFRICA, 6b-u7?7
UuANUA, ob-0305
SOuTH AF-KlCA
JCHAN'.F. SBUKG. 65-0077
ANTARCTICA. oS-OlhJ
CANAbA, 65-0441
NINTHS AL» o'j-0329
OuTARlO. 65-0044. 65-0050.
HAVERFUKDWF5T, b
JERSLY, 65-U295, 65-OjlO
KinDERMINSTtR. OS-037D
rt Il.Nll'EG. 6b-l"'3bH
b!.-0l9o» bb-0300
Gt li.',A,.Y (/,SST)» 65-U014.
t.'_>-j03y, 65-0086, 6b-00'J6»
cb-uOya, 65-0099. b'j-UloO.
t,5-':174, (35-0175. 65-0176.
tO-0222, 65-0236. 6b-0270.
, 6b-0h60
;. 6b-0'402
LUOF-.F. 6b-013b.
6b-03t.l
HAMbUi'G. 65-0387
MuNIC.i. bb-0404
STUTTGART. 65-0152.
65-0290. 65-0377
bL lUENAU-GEISWEIU. bb-0513
uiUkUF."'OUTh. 65-0411
BRADFORD. 65-0400
CARDIFf . 65-0620
C,,EADLt.» 1)5-0274. 65-02dti
DERbY, 65-0390
[!Uc5LIl/» ob-0059
DUDLEY. ob-of>72
EDINl3Ut-'.;,H. 6a-0^3fa
ENGLAND, 6ci-U45d
EPf^OM. 65-0527
EUTLL. 65-03^7
GATLLY, 65-0274, 6S-C288
GLASGOv-.-, 65-014.,, 65-0412
HAMMERSMITH. t>5-0134
KIRKbUl-TOlJ. 65-0068
LEICESTER, bb-0^59
LIVERPOOL, 6j-'01t.q
LONDON, 65-0081. 6b-0084,
65-0391, 65-0715
MANCHESTER , 65-0062.
65-0070, 65-0^43
MIODLETON. 65-n^ll
OLDHAM, 65-0154
PORTSMOUTH. 05-0412
SCARl^Ol-OUGH. fa5-0078.
65-01PO. 65-0171
SCOTLAND. 65-0379. 05-05(44,
65-Ob31
TOTTENHAM, 65-0^50, 65-0^51
TOULON, 65-0153
TYSELFY, 65-0671
WALES. 65-0442
K/EST BPOMWICH, o5-0459
WEST Hf nTFOPDSHIRF, 65-04f 4
rtHEATLlY. 65-0351
vVHlCKHAMi 65-004^
WlTHYDur.H. 65-0436
HUNGARY. 65-0 5R3
ITALY, 65-0188. 65-U204.
65-0224. 65-0280
TRfNTO. 65-t;086
VENICE. 65-0143
NETHERLANDS, 65-0144, 65-1)277,
65-0297. 65-03U2. 65-0500
AMSTERDAM, 65-0103
HA^RLEfi, ,,5-u32u
HAGUE, nb-0405
SWEDEN* 65-0056. bb-OOob.
65-0240
STOCKHOLM. 65-0^.36
SWITZERLAI!!.-. 65-OHo. 65-015^
BASEL. ob-02U3. 65-0227.
65-0733
GENEVA, 65-0393, 6b-0'40d
' OLTEN, -i5-P223
VILLF.TTC, 65-02., t>
ZURICH, 65-0147, 65-0315
.OIA. 65-n557, 65-Oo58, 65-0566
i A
tit
«/• » o -UbP'O
l-LLMl, ob-0637
1 A , hb-^fldO
hAlf-ri, bb-0040
iLi AvIV. bl-'i040
JAMAICA
Ki; u'.TOti, Dt)-028U.
JAPAN
Tui Yo, bb-'Jl7''
MA, l->IIAi L
ob — jbo4
203
image:
-------
Geographical Location Index
SOUTH AMERICA
PERU
LIMA. o5-Gb79
THAILAND
BANGKOK, 65-0275
UNITED STATES. t>5-0114, 65-0182.
65-0216, 65-0217r 65-0230*
65-02b2» 65-0256. 65-0304.
65-U313, 65-0580
ALABAMA
MOBIL , 65-0287
MONTGOMERY, 65-0139,
VvtTUMpKA, 65-0602
ALASKA* &S-0460
FLAGSTAFF? 65-0598
TUCSON, 65-0130, 65-0140,
65-0621
ARKANSAS* 65-0651
CALIFORNI » 66-0009* 65-0064,
bu-0073, 6b-0117r 65-0162*
65-0587, 65-0665, 65-0700*
b5-u728
ALAMEDO COUNTY, 65-0687
ANAHEIM* 65-0079* 65-0170
BERKELEY, 65-0492. 65-0596
CONTRA COSTA COUNTY*
65-0688
EAST CLIFF-CAPITOLA* 65-0512
FRESNO* 65-0032
LANCASTER* 65-0479
LOS ANGELES* 65-0011,
6b-0012, 65-0095* 65-0104.
65-0137* 65-02t8, 65-0588,
65-0604* 65-0607* 65-06tO*
6b-06t8
MARIN COUNTY* 65-0689
MERCED, 65-0010* 65-0247
NAPA COUNTY* 65-0690
ORANGE COUNTY* 65-0208.
65-ObOO
SAN OIEGO* 65-0487
SAN FERNANDO, 6'j-0273
SAM FRANCISCO, b5-0l84»
65-0635. 65-0685. 6b-0686(
65-0691. 65-0724
SAN MATEO COUNTY. 65-0692
SANTA ANA, 65-0085
SANTA CLARA. 65-0478
SANTA CLARA COUNTY, 6b-0b93
SARATOGA, 65-OObl.
65-0052. 65-Ou53
SOLANO COUNTY, t>5-0694
SONOMA COUNTY, ub-069b
WOODLAND* 65-0433
COLORADO
AURORA, 65-0004
DENVER, 65-0131, 65-0177,
65-0591
CONNECTICUT
STRATFORD. 65-0352
DISTRICT OF COLUMBIA.
65-0113
FLORIDA
BROWARD COUNTY. 65-0340
GAINESVILLE* 65-0107
MIAMI. 65-0415
MIAMI SHORES* 6t>-0317
ST. AUGUSTINE. 65-0055
ST. PETERSBURG* 65-0122.
65-0293. 65-0595
SANFORD. 65-0097
GEORGIA
ATLANTA. 65-0367. 65-066(,
CHATHAM COUNTY. 65-0662
SAVANNAH. 65-0106
SAVANNAH COUNTY, 65-0662
GREAT LAKES, 65-0423
HAWAII
HONOLULU* 65-0425* 65-0601
IDAHO, 65-0420
ILLINOIS. 65-0016. 65-0231
CARBONDALE* 65-0108
CHICAGO* 65-oo34* 65-0035*
65-0245* 65-0461* 65-0494.
65-0523, 65-0618* 65-0680
EAST ST. LOUIS. 65-0185
ROCKFORD. 65-0192
WINNEBAGO COUNTY. 65-0189.
65-0190* 65-0191* 65-0195
65-0194
INDIANA* 65-0528
MISHAWAKA* 6b-0t,33
IOWA* 65-0232
DAVENPORT. 65-0249
KANSAS
DODGE CITY, 65-0359
JUNCTION CITY. 65-0069
LAWRENCE, 65-0490
LYONS, 65-0420
TOPEKA. 6L--0471
WYAIMDOTTE. 65-0150
KtPTUCKY
LLXINGTON. 65-0355
LOUISIANA
NEW OHLEANS. 65-0186
65-0233
TtjLANfl. 65-0178
MARYLAND
COLLEGE PARK. 65-0056.
65-0149
RIVERDALL* 65-0058
KOCKVILLE* 65-0334
MICHIGAN
AfjN A BOR. 65-0448
CLNTRAL WAYNE COUNTY, 65-0373
DETROIT* 65-0357* 65-0366*
65-U368' 65-0707. 65-0720.
EAST DETROIT. 65-0157
KINGSFORU. 65-0140
204
image:
-------
,1
i',
•\.ViSA'.- CITY, 6b-Ui7.
. ..0',rV'» t>'.-0261» 00-01,19
b , . Ju'_,rPi'» u5-U027
jl • LOUI'j» 65-0136
6b-u021,
i.UTLL'.-LsLGOMIUGuALLr hb-
CAL(j,vf LLr o'j-Oblb
"...IMIT.
it anf\. \
;,t xic
A'.TCi-. IA»
• /'T,W/ Ar
,, .Ff-A. -;.
b» ub-0,_ln»
LO^'G I',LAHP> 6fJ-nl
iJc«; YOi K CITY» uS-
6b-0(.36» Ob-0uj7r
CA FALLbr ob-Obi-7
ONAWAuDA, 6b-0u73
OY5TE.R .5AY» ob-u.570
MEijEC TADY, 6b-l _
ST CHLSTFl COU'.TY, ti'->-.pS?6
I'ALLIGH* 65-Ub9t:
A'P'STOfj-SALi Mr ub-Uiin,,
» 6b-063'+r t,b-n7l6
AKHONf o5-07l9
AVHLK57 » b^-ul?.,
HALT I Mf •(;£.» <'b-0,09
CI'JCIMCATI. ob- if)77
CLFIVELAUD? io-0u?,*
COLUM31",. 6b-0<4b3
FPANKLJil COUNT Yr t,S-fc/rj
MlGDLElOrtlir ob-tJ' /> _•>
NL'v" CAf'LISLt r 6 ,-Oo2!1
TOLEDO, 65-!-b22
ORTOOu, bb-0094, b')-, 3.ib
LANE COJMTY* ,,r-.-i)S6b
Geographical Location Index
HCMNSYLVAtJIA, 6b-04,,7
ALTOONAr G'J-U2fel., bb-b20 -
MOMONGAHLLA KIVL,<, b'--0'L_-(-,
MT. *OLF» 6b-00oo
PMlLADr LPHIA, 6:>-OfiOr
READING, 65-uo7n
bOUTH CAROLINA, bb-LUc>t.
CHARLESTON, 6b-,;i3u,
6b-Oi+77
TCMUESSEC
ASHLAND CITY, f>b-0473
NASHVILLE, ob-0^73
TFXAS, 6b-0110, bb-0702
tL PASO, 65-ub2':i, 6b-Uf.2,-
FORT WORTH, ob-ub29,
bb-0b!6
HOUSTON r 6cj-028-i
SAf! ANtOIJIO, 65- ,613
VlRGllJA
RAPPAHAflNOCK RlvLR, bb-0H37
•J, JAtj A, ub-0'+37
65-048^, 6b-U6bC
i PPL; 5irof
,,hi LLL G,
•.. i ' C 0 'J I N
KLTTLF MOJ.AINF STATL F
bb-Cktoh
oS-' 3b3, bb-ObO
Pi YN.O ,TM, bb-0<4bo
205
image:
-------
SUBJECT INDEX
.Ju ,1 . L..u'--;ri,,.
->t._ b.'lV'iY - , ; ACCli.,_.,M I-V. VLi.l I "I.
Au -,i'.r-Jn. ri-ji.
Sue- .-,J , '>wh"" (
ML;\CS}';,CL '. -luA'X'i
•jt-c. V "0_ C -AFT
ciji\ lCoi_1 u; . L /. AC i _~?
jo> ^ r.' .,-.. t» ub-.«i%'>
i-< A j P ^ . • / L i a ; — i i. i- 0 ' ' o ~ f .-- 0 7
1 ^ r>Oi.i..uTi u
(30. ;.;,., -AST...,, bL-Oict
CONTROL EuUIFrtuiT. 6_>-'. 34lr
ub-C.389
UU' Pb. o5-0165
DojT COJTKGL. 6b-0')^o» bo-03
LA,..S> C JK t_'«.IN > n' -uO> 4
Ji'A^f u ^ '• IS L> '.iTl— -'J'O j ' OJ— u
T ^ ' ' u ^ ^: -' ' o ^ *~ ^ ^ cj c
• '.{•il ' ": 1 C i./ V I A '
,.'. U.
-i j.^»- • . •. '. '• ». . •>» •'
t . .' .- . f':» OJ-' .•iJ't
_J I 1 i. ' r t-L.- r*j7
,Aj)E OK17/U1IC l.'J/«L'lN
,-l.'i_ •' H '^'; .w j T"
:,,L, L -US ,o./jl',( . '-'
nb- ji'.i i,.;-C A: I. '
.-.!)_ 7: ;, ,,J-;i'll,»
riL)- 71' r 'j- Ti!1 '
uL>- 7j,^
'( i 1 ICi./'L('t\ i,v ,t '}' . —
(.:-,, 71 - r,j- ;7?.v» i- ^
,/j- -,.<.;"+' i ^-:,7^7f 00
•j'\i IT1' T i_'V;: '!" 3 uLli -.^--
(,U!i M'J.J'
iL-^-t /l Y, bb-OLu'l
AUTOi-'.G-JLtS. SCHAP
S CO'JCi-.' , jl':'' r o_-Uij27»
HTil-TZi.TIC.o ob-02b2' 6^-b25'
Sf.L Al_b.i METfLSf bCHAP
ELIjTr 65-0323
vASTES
COuLECTIONf f,5-OOTu» o
fab-014?
rjlS^OSaLf o'J-0682
Stt ALbO GrU:'')Ir/ii RE^OCTlOf: OF
OS'JT'-" bYSTr
^EL COLLrCTK J OF .vASlES
CLEANUP PKOC'^A.-lSr 6b-u67'S
fc^-no7G» 6t:-0b77r 65-0679» 65-0680
( LI >ATL
EFFECTS 0,, 3ISPoS»*i_ f-'t.TH')bSr
fa5-0184» 65-0309
COLLECT I 'I,-, OF /.ASTES
"'ULK CONTAIiJErtSi 65-OiJ5» 65-0459
CHuTF SYr>TL", 65-C147
CCbTS» bS-OO^Sr 6b-00j0r b
5-04'5'3( 6b-0fafl7»
r>-0o-ia» 6S-069C r
6^-0720
f/J VERSUS Cj'-U PICKUP.
.:'.T' ob-0123, 63-012**
c:, 6b-0l22» 65-0317.
K jCYr 6b-00r>l. 6;-OC52.
oj-ur, -?. 6b-006^. faj-C13r»
05-0160
rA, c> 5 — o u T 1 . 0 b — o / 1 '+ .
uh-0257
LI- i«Cfv j.,i '3"i K
.i 5 — ,j ,,i-t . ',-j — i • l(
;b— i b .» Lib — i,1 'I
b — . ic/i. . t. - — L1 )
206
image:
-------
Subject Index
i,t Gi-' • !»
„/->-. Ill
r't_ OJ, . i ^ F f,L»— ' ' 1 u !'- , 3.; F 'ii--' '.-.!.!» 03-vU >
.-?)-. .i-"1- 7 » t.')-.'ljf.' uj-06o
o"-i ..lii i i^-Ci-'i1?' u3-Co'^
.
U: L 1 1 ^.7 h,.. a S . »j o- , "! 7 •_,
- b — i j of' » ,'.,— " ib7
' L , A (,. • b ' - 0 J -t /
oCuC] i. vrcjTL ' tj^.-^i'j i
So- V Y _• ' o'^— j,j7.,p 6LN — oi
bb-',13u»
Cb-01'*L)»
c. -• — ,... G ' !.. ' -i 6r! • b j — >.>
•-.,, It, . :' Y' t -,_,-" in'"
CO r-C I ly<
t-'nt'It .- r f r i _i — i_.'H>,j» uli— i.'
T L.A. . f-
CO,ir-I,jED
05-0^9"
rCi-!,nAr;tp ,vITh OT.HtK DISPOSAL
,>iFTl!0:;rj» 65-0270 F 6^-0312
COSTS» e^-GUaC'F fir.-o2'j9r 6fc-
(St-0287, 6j-029^»
65-G2fi2»
h5-02'j2» 6 1-031 iJ
6^-0^.90
6^-0277, 6^-
jT» 6^-0310
^Y OP'J:lf 6^-0^
i^n VCc-ETAGLL W,,STt:S»
CAS ro,< ,,"nONF 6r--030jF b
GE;;r5;,L riiCi'SSIO'v, OFF 6b-C£58,
of)-Ue:7S> 6S-029C, » 6^-0296.
ti?-030n» 6^-03r6» 6 3-0313
GLASS CECOf-Pc 5ITIO ,» o5-0299
HYulF.iaC ASP. CTSr t>5-j2fl9r
•,r)-0;in7
INSTALL/XT 10'slS' 6^-0260 F 6b-u296»
6E5~u2P-.F 6b-029of
65-03lt
OSITIO.j
co
fjU .» 65-0; 10
6^-0277,
6 ^-
nT j.Ci't. '•'< CUJITRYf t/o-(
ob-i I'-IF f,ti-.i2i)b
.Nl iC^L.'iN I 'ICIP.'Lil (
1 1. .-..it, » 6:.i-ur«s4-
SOIL I -.[n-C
r-027(-
luLOGIC^L
ob-;. ,'9' F c-b-i ?97
.^LL ;w.»-r.f jb-01J»?F j
u',5- .7f_.F oJ-i'io-J' o J-.
207
image:
-------
Subject Index
T, -Pf ro>,Tl/>-Lf ;..r--U£:';9' ..5-03Q7>
bb-,.,,,Gr'- » •; -,-3.509
.' '
SEL SfSTEMS ANALYSIS
-L ST
COST'j
uiSPiS,^ OF ,
w3-'?i"43» cJ
AiCl.JL.AAUO!>
ob- , i(, I
IlML.U'iT'.I "L. ,«
D5-0338
b5-0076
65-00,'/i> 6
T CASfcS
SfL LLwAL ASPECT CF
PEu'lCTIOi OF R
lTb» 65-0453 > fa
65-0416* 65-053j
65-Oj,17
lSE^ScS
COUFr«t.i-!C£; r ^5-06bb> b.S-0666
TRANSMISSION! 6b-l-656> 6b-C666>
oS-Ob7"5
SFc. ALSO PUI5LIC HEALTH
-ISPOSAL OF AAbTt.S
-'.'.If.E APf'ROAC" TO WASTF
i'.iArJAGf''LMT> 65-0081 » 65-C703.
65-Q71J, 65-07,:0» 6
65-0727
A H TPAUE' 65-0713
nFr:RE Ct» f,5-007o>
65-UlCr' 6b-0171> 6r
6b-018Uf 6
CONTRACT* 65-071U
COST?> 65-0114> 6b-03-;l
DEAD ANI'IALS, 6b-'J?l3
65-0467.
65-0501
GENERAL DISCUSSION OF > 65-0072,
6h-0086r &5-009l>
6b-0116>
6b-0182.
o5-Ul'jl, 65-0196, 65-019B>
05-019^. 65-0214, 65-0216,
b5-0218> 65-0416> 65-0426*
65-0588> 65-0686> 6b-0708>
b5-07l3, 6b-0714, 65-0720,
o5-0727» 6S-0728, 6b-0730,
65-075?
GOVERNMENT FACILITY, b5-0121>
b5-0l83> 65-0435
HISTORY, 65-eoai, 65-oi92>
b5-0lg6, 65-02H6, &5-0686>
bb"-070l
HOfa FEcflNGf 65-Cll3n
65-0192
LArtS COi CEi
65-0189, 65-Qa08i b5-0b87,
65-0638, 65-06P9» 65-0690r
6j-u£,91, b5-0692» b5-U693,
An Si ATE (U.S.)
...5-0110, ob-0210> ob
F'kiVATt FIRMS, 65-0093
PUbLIC rILALTHr 65-0&b9> 6b-066u
RtCRLATIONAL A^EASf fab-0079»
65-0092> 65-0170' fc.5-0b51>
65-0657
KEbEA,,CH» 65-0117
KtbE,u'<(.n |N,Ec^S, 65-OeU2, 65-Ob-i
KUI'-.AL. ;\'*if-S, bF-0£.2h> o5-071o
SAi-.IT/-, Y LA, ,^,1- ILLS' ba-06U7
f.)5-01Cti>
LA,,S
; PS
(•'*. Ll,,
: Iu,.» 6rJ-u015
ob-til75» ob-01o6>
fab-019>
SLL .,1
v.KiN.1 '.
i,! InCl.Nl-.rJ'.TIu
208
image:
-------
Subject Index
&£. it. . i L'lSCvoSlOi ' Ot- i rib- 1 olio'
b5- ,_9,>i cb-0o97' bb"-n7j'-,,
65-, 711, 65-07U:' 6b-f.72--
lK_,Ub1> .«L 'A
65- .,-,'• •-„•
'LV/is',_ ' !><.'; , \cCLAi' ,ATiu. • L^—
b 5 — c :^ 6 6 ' i" i : j — o b o ( ' ' a b -~ u b / '_ ,
l.QUIPMEHT
FXhI"-ITlON» f 5-0060 » u5-
0*1-0118, 6b-0l20» 65-
^Al'iTE.NAf-'Cb> 65-OC42' 65-0126'
FEES
COLLECTION AND DlbP05AL» 6c>-00;-,8»
o^-OOO'lf 6^-0107, 6j-0110r
65-0?lO
COMPOST 'VSf 65-0?9b
MANURE ,vS. 6--0232i
65-C236
FINANCItJG
SEE COSTS
FIRES
FLY ASH
DISPOSAL' 6b"-05'+0» 65-0549
UTILIZAflO1^ 65-0&42
LlGi -TWEIoMT AOGPcToATEj
65-0545» 65-u547> 6b-0b7(.
FOOn PkOCESSlNo H*VSTFS
'r 6b-0r>57. 65-3558 »
6b-1656» 65-0666
FFr-CCV O'
LA^OO;JS» 6b-. 429
POTCTO, 65-OS56
'3l 65-0556*
65-0575
ifFFFCTS UF
6r)-OCl'">
PO|_LUTIOr^
'LASS
I OTTLtlS
CHUSriliiO, 65-0319* 6b-C32b
COl- POSTI'IG. rSb-0299
'.ij SoPP'JHT
F-UL'LL L
t-iuo FL_I j,
c. PU LiC HL.".L
T;.Rl '•:>
ok jt oF t,/,
'.5- ,'0,.,1» :.b
bPC^;,L Of. bP.'Ct CKAhT»
i-A] UN, Cf KT -AL
C ",CI'ES f- ««A
or-
..iOLi* i" , .'S'h, >t t, .-c.r--°7
CAi »c. J T Y, o --J.-.47
Ci_.,T, .u ror.,.,0u» f)c3-..o-»6' f
Coi,fJI.,LJ wITn C'VipOSTi j'3» e
CL..P,,ttJ r.lF, , - uvITA^r LA.v.
•-•b-vj. .V
^.OuF^, __ 1 1 » ._ i- ,3j3
Cu. .Si •>..,•; I iO,., t'j-;.-T'j» 6b-;
ELECTROSTATIC ,'HEC IF^
b5-0iel
EXISSIOUS FKOi«.« fab-L'
o5-0352> 65-u354t ob-0358
CKUSriERf bb-0337
FILTLKS. 6:,-0337
GRATES' bb-o37fS, or;-U378»
bb-i)3i'ib> 65-03^0' uo-04J:
-
FLA''F ChAMJEh PROCESS, 65-C407
LLANINO' 6R-U337
ASH, 6b-0l8l, fa5-.J.?b8
FUu:iACES' farj-0342' p5
209
image:
-------
Subject Index
GENERAL QISCUSSIOFM OF, 6b-C333,
65-U331:'. 65-0351. 60-0363,
65-0390 , 65-039b. 6^-0403,
oS-Oi+O'+f 6b-040b. 6a-0406
HISTORY* 65-0363
OPERATION. 65-0102. 6^-0171,
b5-0346» 6b-0370, 6O-C379,
65-03fi5
PARTICULAR COUNTRY, 6^-0203,
65-0206. 6b-021b, 6:j-0222,
65-027°
PARTICULAR MUNICIPAL!!* AND
KLGIOi,"
65-GH3. 65-0211. 65-0229.
65-0284 » 65-0334.. 65--G340.
65-;j342> 65-03*47' 65-0349'
65-0353, 65-04U2. 65-0403.
65-0«04» 65-0707
SALVAGE, 6b-;;379
SEPARATION SYSTEv &5-0374,
o5-0375» 65-0400
SLUDGE. 65-0343. 65-Oo54.
65-03D1*. 65-0365, 60-038t
SLU~>GE AND Rf-rusr. 65-o3hi
SPtCIFlC'TIOt 5» 6b-Q304
STAMDAK'-.S. bc-033';)
SUKVEY, 6D-0707
SY'jTTM t UESSELDORP . bb-036!1:
VON ^OLL SYSTEM, es-0399
V'ASTE HtflT Ul ILI7ATIO,4» 6b-0l7,
65-0349. 6b"-C350, 6:,-0371,
65-0378. 65-0379 r 65-0386.
&5-0405
OESALlWI/ATICI- Of7 ,vATEK,
65-0181. 65-0361
r ON SITE
AIK POLL'-lTlOf, CONTF 65-0212. 65-0356
CObTS. 65-0396
DESIGN. 65-0392. 6b-0397.
t.5-0401
KObpITALS. 65-0209, 65-0377
INDUSTRIAL WASTES' 65-0338.
65-0537
LAv,S COfjCLRNI'JG, b5-Oj(H
FESinENTlAL. 65-0328
SMOKELESS. 65-0396, 65-0397
WASTE HEU UTlLIZATIO-si. 6b-058,+
INCINERATORS.
ANIMAL LISPOSAL, nb-ujG?
BULKY WASTES, b^-035-j. oo-0362
TELPEES. 65-03,';6. 65-0^)5
WOoD ViASTt. 65-0357
bb-0<'4.70>
bb-(. ;ei
ob-
->'. ' 0-J-i
ob— >,, '_, If » Owi—
ob— Ci4j
'» 65-im,:. 5»
— o a 4; i
ChEMIwAL. 65-CKlOr 6b-;4
ob-0473» 65-0490' ub-0502.
6b-CbOB. bb-ublh* bb-ub25»
ab-0527
COHiJNtL wITH .' UlJlClH^.L rt/>STtbf
LLL.CI, tPLATi^v.-
t ' r^;
U -' — >_ , J c
rw>. • '. w t'Ar. " 1 1 1,. .
i cur. r "'
_>5-i (6!'f .j^-C'tb!!. 6w)-04-ol .
6b-;-, -Jb
s)r. -E-r I,L ijlSCvJj^iO:. Oh. 6->-'_ tt.i_i»
oc.~ ,L '"'-;' t:-j-Oi3L' t)j-'l 'u
jKOU.a . ft TuK HuLLUl 1C,,. 6^-, '4Oc
i'A^/n\; '-'.J-3. v b-'j^c'y. ob-Oct;- i
HYDRAULIC TRAUSPOuT
FLY ASH. 65-0477
INCINERATION, 65-0172, 65-0421.
65-0465
IO.J FLCTftTIOf . 65-044-j
IRRIGATION. ^5-0446. 65-0^95
LAwS CO;-,CEKNI!-!G. nb-0u05
-SY, 6b-0.*21.
65-04f-3. 6^-051':
•'EASUtic.: FNTSr 65-0427, 6b-i)451.
05-047n» 65-0471. 6,,-047't.
b5-0611
•/EAT PACKING PLANT, 6b-o5o9
METAL TC'^ICITY, 65-0413. 6b-04J.4
"-'ET^LS. 65-0504
"I.-lT'J'o, 65-On?6. 65-0-t57.
65-05?4. b
210
image:
-------
Subject Index
PAPER AMD PULP MILL. o5-Oi?H»
b5-040t?r 65-0419, 60-0441,
65-04146, 65-0447, 6)-C452,
o5-04fc?» 65-0530, 60-CS?5
rCCCVUr^Y. t>5-0214» 65-0410.
65-043'* t 65-0525
SA ,r>UbTr 65-i 162
lO'.' 65-0409. 65-042
NG E..'JIP'"LrJT» 65-j^b7»
L A A _
STOP'&L, 65-i 059. 65-ulC5
TEXTILL '"ILL, 55-0452. &5-0516
TRc.«Tf'!tfjT» 65-0237. 6^-0412.
b5-U4l3r 65-041 b» 65-04l6r
b5-U4l3, 65-042't. 63-0436,
o5-043°» 65-0440, 65-0441,
65-0446, 65-04^. 6j-045fc,
05-0462, 65-046.* , 6o-04G4,
6b-048t<» 6-_>-048l .
60-04fabr
65-OLfi^, 6--0501. 60-C'JCb»
b?- 050?, 6b-05''>f>» 6u-05u9i
o5-05l2, 6L-0513» 6^-0514,
-J4if-» 6'. -0429, 6'j-046C,
'AVMTP PCLLUTTOU, rj
V.Ef OXiT'iTiO . 6^-'J45-4» b5-04b(,<
0^-047^1 6L-0517,
65-05^6 r 6f--0b3'j
pltS
5ti_ SAFETY A, T' ACCitJE.iT
^ .T. U,
i"r. i If !.» f,0- )11"
,_L nOsi ITAL5
,
-", , I'K^UL s'-ii^C \./-?_i-C!-tj3
MLwAf. c«', >. Tn, ro-i''Jli4» ob-r
FL\/f.' fiOC£SiI,.ii .(AST^j, 00-
-AiUi.;- T L.AT '•-'. I ' 6h-Ui"U
i_HiJL. KiICi.,, .Tl'1'
UO 'P.'bT UbC • o' ~i'?67
LAN.JHi.Uo - _.i_:T S^.,IT^,,-;Y u^'atri
Al.TI-LI r I,".". t,L.-Ouf19. o5-
CGLU.s,7I'."J ."i ,.n-STCS. >5-06
t..b-,:.ll. u'j-s il^' 0.,-Oui:.
t,5- Cv.i
LL P';ir i>-0,l, ., r b5-!iUc.J
P/ 1 r. . I , (..5-...J ji
t-L.vLiC i'i *'Ll, , (o-f-"'o.y, 0:1-'.
;>,. jl I ' . 1 L.A' ^PILLS' oj-Guuc
L>Ci_I~ .-1c. 7E ^ •.IPOS'-L » c5-0,K
'5-c1 fl •» f-i-ii' C1^' 65-vuJ r
oo^i. , ^,,rt
u5- ,'-2- .
u5-: i.0 P^ -- ",i- Jl~ ../L'TFT.' Dj-.ioc.Jr
6b— ..i54, 'iii-o/li. . oj— j71r'»
c5-0 /22. . 5-'7il
SANITARY LANDFILLS, j-ouio.
b5-00£5
oC'.^t / .'To^ ^ i ., b . 65— ' ''< <^7
LICEPSt'S. 65-003,!
LITTER
CAuSFTS OF. ft1; -0011. 6j-067C'.
fLRSr t5-067D. u5-
bS-Otjgli o'i-06'33
FX7PATt"Pnfc.ST' TP
r-t.\r:fiT
COLLECT Annj AJ 0 JSPQS^L M
65-Ob'i?- , 65-0693, 65-0694,
6?-r)o9c;i 6b-0731> 6j-07o2»
b5-07n3. 6'. -0714. 65-0719,
b5-07,-;n
nFrKL.iCE 6^-0717
r" 6C;-071
r-ISCi SSIOC OFr 65-^
4, bS-0713. 63-0715,
6L.-073C
image:
-------
Subject Index
PARTICULAR MUNICIPALITY AMD
REGION*
65-0685* 65-0686' 65-G6S7*
65-0688r 65-0689* 65-0690*
65-0691* 65-0692* 65-0693*
65-0691* 65-0695* 65-0703*
65-0707* 65-0715* 65-0719*
65-0720* 65-0721, 65-0724
'ARTICULAR STATE* 65-0700*
65-070?* 65-0716, 6b-07,ie
.AN'tlNG* 65-0099* 65-0685*
65-0696* 65-0697, 6b-069R(
65-U699, 65-0700, 6b-070?,
65-0705* 65-0706, 6D-0707,
65-0708, 65-0710, 6O-0711,
65-0712, 65-0714* 65-0717,
65-0718, 65-0719, 65-0721,
65-0722* 65-0723, 65-07<;4,
65-0726, 65-0727, 6b-C728,
65-072°* 65-0731, 6j-0732,
PRIVATE FIRMS* 65-0696, 65-0709
URBAN PKOBLEi-'S, 65-06^7, 65-0705*
b5-0706* 65-0722, 65-0724,
65-0727, 65-0732* 65-0733
SEL ALSO JURISDICTION! AREA-WIDE
APPHCACriES TO WASTE MANAGEMENT
MAiviURt.
OUuRS
OIL
ru. At
UISPOSAL, 65-0230
DKTT i.O, 65-0234, 65-Uti'J
HuALTIi ASPECTS' 65-U2jt:>* Ob-0bc?
IfiSLCTS* o5-ut>52» 65-Ob5j,
o':>-_.&54* oS-0655» to-G6bf »
o5— ufo63
L.A, 65-02b9
.L. (i-'>/,.*l "Uw PAVLOAO)
SLL TxAi.bPOnATIOrj Of ..
NAXiiii.'t' PAYLOAD
CKUSHI..G, 65-0316* eti-j3l9
, 65-0244, 6b-02'3t,
1, t>b-055l« ob-0'j6c*
65-0243* t>5-
SCr-.Ap, 6b-
AUTO- O
SEE
LQUiPME^J* b5-0539» 65-054^*
tr_.-05<4.'3, fo5-05bb» bb-0b6l,
oS-o5o2, 65-0567, 65-0571
Ml) .'It.iFAL j£.r-.VICh.S
Stt COLLtCTIO.j OF rtASTtSS
C.ISPUSnL OF V-ASTFS
OCtAu L-ISf-OS'.L
Mui 4 1 C I ,' A L "•';• b Tt S * 65-0100
SC-7
v't.i Y, 65-0007, 6b-J54<4,
ob— uybO* o5— Ol353» 60— Obb7,
oS-u^.bh* D5-0559* bj-O^uij,
SEPARATION F^OH DOMESTIC
SPECIAL COLLf.CTIOM METHODS*
bS-OOsO
PAPtiP INDUSTRY WASTES
B.O.D.* 65-0409
COST OF TREATMENT* 65-0409
RECOVERY* 65-0573* 65-0585
WATER POLLUTION* 65-0409
PAPER SACKb - SEE STORAGE OF REFUSE
ACCIDENTS, 6r?-0156, 6j-0661,
b5-0664, 65-0667, 6-J-0670
FMPLOYEE-M ANASEMF.lv. T RELATIONS*
65-0111. 6F.-0136
DISC. .SSION OF,
65-0723
SALARIES* 65-0110* 65-0159
TRAINING, 65-0155* 65-0639*
65-0640, 65-0644, 6b-0&46,
65-06«B, 65-0649, 6b-0650 ,
fa5-066l* 65-0668, 6^-067C,
65-072?
PESTICIDES
DISPOSAL, 6^-0533
6h-0b31, 6^-0532,
65-05^3
TlbPOSAL* 65-0534, 65-;i53^»
65-0537
PIPELINES, 6^-OOr4, 6b-0030> 65-0115
PLASTIC
INCINERATION, 65-0071, 65-034^
SAuITARY LMNi FILL* 65-^071
PLASTIC COUTMNEKS
SEL STO,<".Gt (;F REFUSF
POLLL'TION
SEL AIR POLL: T ION » A'ATER POLLUJI
POULTRY
SEE AGRICULTURAL AASTuSi FOOD
p^ocEssir^G WASTES; , ,ArajRF
PUBLIC HEALTH, 6l— 0423, 65-0451,
65-0473, 65-0474, 65-0497, 65-0608
212
image:
-------
Subject Index
CONFERENCE. 65-0651 , 65-065&,
65-0666
EDUCATION OF PUBLIC , 65-0729
GENERAL DISCUSSION OF, 65-0659
65-0660* 65-0673* 65-0674,
65-0702* 65-0706. 65-0718.
65-0727
LAWS CONCERNING* 65-0457.
65-0494
OPEN DUMPS. 65-0186. 65-0457*
65-0593* 65-0596. 65-0601.
65-0602. 65-0603. 65-0615.
65-0669
RECREATIONAL AREAS' o5-0651.
65-0657
SURVEYS. 65-0662
SEE ALSO DISEASES
PUBLIC RELATIONS. 65-0222. 6b-o704,
65-0731, 65-0732
EDUCATION OF PUBLIC. 65-0678*
65-C679* 65-0681» 65-0705,
65-0709, 6b-0723» 65-0726
LIFTER PROBLEMS, 65-0675
65-0&77. 65-0678' 65-0679
65-0631. 65-0683
SANITARY LANDFILLS' 65-0709
PULVERIZING
SEE GRINDING! REDUCTION OF WASTES
RADIOACTIVE WASTES
UiSPosAL, 65-0420
STORAGL* 65-0420
SEE SALVAGE AND RECLAMATION
RECREATIONAL AREAS
£>LE COLLECTION OF WASTES*
DISPOSAL OF WASTES!
STuRf.GE uF WASTES
REDUCTION CF hASTES
AT TRAt.SFER STATION, 6S-01&3*
65-0329
BOTTLE AND CAN CRUSHER. 65-0316.
65-0319, 65-0325
BUi_KY ,,ASTE5 SHREDDING, 65-0315,
&5-C326
EQUIPMENT, 65-0170' 6S-031b,
65-0316* 65-0318* 65-0319,
65-0323* 65-0326' 65-0332
FOLlAGt.* 65-0517
FOR COMPOSTING. 65-0273,
65-0331
PC* INCINERATION, 65-0072
GONARO SYSTEM, 65-0320
HAMMER,, ;ILL. 55-0329
PARTICULAR COUNTRY, 55-0270
PULPING' 65-0318' 65-0319.
b5-0322
PULVERIZATION FOR SANITARY
LANDFILL P 65-0327
ROTARY DRUM, 65-0322. 65-0324,
65-0327, 65-0331
VOLUND SYSTEM 65-0321
SEE ALSO COMPACTION
REFUSE
CLASSIFICATIONS, 65-u200» 65-0725
COMPOSITION, 65-0072, 65-0098,
65-0116' 65-0197, 65-0270*
65-060B* 65-0725
ANALYSIS, 65-0211, 65-0219,
65-0220
DEFINITIONS* 65-0176* 65-0725
QUANTITY' 65-0114, 65-0197,
65-0216* 65-0220, 65-0460,
65-0608* 65-0691* 65-0692*
65-0693* 65-0694. 65-0695.
65-0725
WEIGHT. 65-0072
REGIONAL APPROACHES
SEE AREA-WIDE APPROACHES TO
WASTE MANAGEMENT
REGULATIONS
SEE LAWS
RESEARCH
CURRENT PROJECTS* 65-0643*
65-0645* 65-0647, 65-0649
MINE DRAINAGE* 65-0426
NEEDS IN SOLID WASTE HANDLING,
65-0028, 65-0723
NEEDS IN SOLID WASTE MANAGEMENT,
65-0216, 65-0641, 65-0642
UNIVERSITY, 65-0639
SAFETY AND ACCIDENT PREVENTION
PARTICULAR MUNICIPALITY AND
REGION*
65-0055
PROGRAMS' 65-0661* 65-0668* 65-0&70
PROTECTIVE CLOTHING, 65-0667
RECEPTACLES. 65-0664
RECREATIONAL AREAS. 65-0651
SURVEYS, 65-0670
SALVAGE AND RECLAMATION
CONVERTING WASTES TO LIGHT
WEIGHT AGGREGATE. 65-0572
COSTS. &5-0579
ECONOMICS. 65-0565. 65-0566.
65-0574. 65-0580. 65-0583
EQUIPMENT. 65-0555. 65-0560,
65-0561' 65-0562, 65-0563,
65-0573. 65-0574. 65-0582
BALERS, 65-0546, 65-0567*
65-0569, 65-0571
CHARGING DEVICE, 65-0552
CONTAINORIZED HANDLING*
65-0548
CONVEYORS, 65-0579
CRANES, 65-0539
FlaERS, 65-0554
FLY ASH, 65-0540* 65-0542,
65-0545* 65-0547, 65-0549,
65-0572
FOOD PROCESSING WASTES, 65-055&*
65-0557* 65-0558, 65-0564
GENERAL DISCUSSION OF. 65-0116.
65-0219, 65-0575, 65-0580.
b5-0728
image:
-------
Subject Index
'_>R.. ACE. 6b-..5<+j.
LIMBER MILL WASTES' 65-0573
,-ETALS' 65-0541. 65-0551'
65-0552' 65-0561' bb-0566'
fc5-0570» 65-0576' 65-0577'
fc5-u561
OIL' 65-058;
PAKE), » 6^-0543' 65-054'^,
o5-ui5n, 65-OS53' bS-0559,
6b-0b6c» 65-0563' 65-056=5.
t>5-Jb68' 65-0574' bb-Gb7P,
P£f-ER AtC PbLP MILL ,-ASTESf
PARTICULAR COUNTRY' 05-0007
PMKTiCuLAK STATE' 65-0720
Kt.tjUcT.tOi. PLA,>.T' 65-0329
REJL/u C.1» 65-0170
SAhLUST' 65-0573' 65-0584
SLUDGE' 65-0411
SUi-Fur, b5-0536
».AoTE LliUOR, 6b-05flb
Stn ALbO AUTOMOBILES' SCRAP
SAi_VAGt i-,ATE,-IALS
FLY ASH? GLASS! McTALS?
i'iIi,i:RAuS> PAPER! KUb.OER; ,VOO.
LANDFILLS
bUlLuL',3 ON, fab-0597
CAiJYONb, b5-U600
COMPACTION' fab-02b2r oi-02b6'
b5-T267» o5-0b'86' b^-0b99'
6b-0606
WITH I iCI^EK«TIOi»,
65-0606' ob-0607'
6b-059o
DLCO.MPOSJTIO,, UF REFub.l' 6:;-
6b-Ub39' 65-OQ09'
to-r 612
CO FACTORS' 65-Oi>9i ' bb
-06l4» fc5-r
h' oD-0599
OAS
OISCOSSION OH » 65-0104'
65-0593' b5~0596'
65-0702* sb-P73C
GEOLOGICAL CONSIDERATION*
65-U596
IfJuUSTRIAL WASTES' 65-0105
LAND RECLAMATION' 65-0266
LAWS Cot^CEHNIivG' 65-0006
LEACHING' 65-0608' 65-0609.
65-0611' 65-0612
PARTICULAR COUNTRY. 65-0096*
6^-0101' 65-017^' 65-0204.
65-0703
PARTICULAR MUNICIPALITY AND
RCGIOi;.
65-0^59. 65-0095' 65-Ol02»
65-0106' 65-0113' 65-OlS)0»
65-Q193' 65-rO£29' 65-U566'
65-0591' 65-0592' 65-0598'
65-0600' 65-0601' 65-0602,
65-0604' 65-0605, 65-0606'
65-0607' 65-0616' 65-0618,
65-0687, 65-0688' 65-0689,
65-0690, 65-0691' 65-0692'
65-0693, 65-0694, 65-06y5»
65-Q699, 65-0721
PARTICULAR STATE, 65-0728
PRE.TREATMENT OF WASTES, 65-0327
RECLAMATION CF LAND, 65-ooes»
65-0266, 65-0592, 6b-0595,
6"5-ObC6, 65-0613' 6^-0618
RECREATIONAL AREA* 65-0586'
&5-0595, 65-0597, 6'j-06l3,
65-0615
RESEARCH' 65-026B' 65-0594'
65-0608, 65-0611
SETTLEMENT, 65-0266, 65-0267,
65-0597, 65-0608, 6j-06Q9
SITES, &5-0205' 65-04ti8,
65-0603, 65-0615, 6b-06cj6,
65-0726
ACCESSIBILITY' &5-0153
ACQUISITIOI/, bb-0;j25, 65-0?24
SUKVEYS, 65-0604
TEMPERATURE, 65-0608' 65-06J9'
65-0610, 65-0612
TRENCH v.EThOO' 65-059^., 65-u59fi,
6B-0614, 65-0618
WATER POLLUTION, 6s-oia9'
65-0194, 65-020b, 6j-05s7,
65-0594, 65-0603' 63-0608,
b^-0609, 65-0610
SCOQTEKS, 65-0150
SEASONS
SEE CLIr'.ATE
CObT OF TKErtT. .t.:JT»
FACILITIES' jj-Coo
OK^A'.IC 'ATT[_H' 65-0^7
PLANT co-'uiU[.u
ob-tl77, 05-0180' 65-0^07,
'jb-i,^2t-' 05-0412' o5-04A'M
"
i ION, 65-Ob7n,
65-0577
214
image:
-------
Subject Index
L/S)C>,,U ,,, TS» ,,;>-i:4
L>v/'tn~'4» 6b-«i4l2
l'AtKC.iIC TfLAT;E!:T, e>;,-U4'i3,
u5-j ,bC
l,t.'431» 6y-ij4bb.
o POSITION, Ob-0
CO
OF
6b-C4l9»
ob-048b'
0'.,-0500'
b:,-0b23»
ob-0<4-12»
ibH^o. Lr 6l-v-lbOr
o'S-L. i-ri^f ^b-C439
W<-;.' I v'tR r 3 jISPCS«L' o-j-
fl,,.3» ob-O^o'-
, PI,,,,. ob-(.. c
o5-.j;,6^» r
65-05l3> 6
65-OB08»
65-049?
UTILIZATIOfJt 6b-0bl7
65-0338»
65-0372' 6b-0381» 65-03B8.
oS-OUdU. 6b-0^86r 6b-0500»
6S-Obl2, 6b-0513, 6b-0530
TH£K"OSOMC RKACLjR SYSTEM*
LAijO SP!',EAUIhG» 65-0^11
ANIS S» 65-0445, 65-0'455.
SETTLING' 65-0422' 65-0425.
65-0532, 6b-05i:l
t 65-Ob?u
65-f)415
TRA'ISPOtJf 65-0145' 6j-0372
65-0419, 6b-04£5,
65-044b, 6b-0447,
6b-0465, 6
b5-049l, 65-0433
TRtATMENT PLANTS, b5
65-044H, 65-0454, 6b-P4t>4.
65-0473' 6b-Q47b, 6b-0496,
b5-0bl2, 6'.,-051b
UTILIZATION, 65-0348' 65-0411'
65-0412, 65-0469
WET OXID^TIO'i' 65-0454, 65-0456,
65-0475, 65-0517, 6b-0b23,
65-0526
SPACE CRAFT
EXTRATERRESTRIAL LITTLR» 65-0684
.WASTE MANAGE ENT srsTL-^ 65-0213
STANDARDS AND SPECIFICATIONS
SALVAGING, 65-0007
STORAGE OF WASTES
CONTAINERS, 65-0010, 65-Olil2»
b5-0047, 65-0055, 6O-0059,
65-0060, 65-0111, 6b-012G,
65-0129, 65-013&, 65-0143,
65-0730
FLAM'iAdlLlTYf 65~u046
FLY PRODUCTION, 6b-005l,
65-0052' 65-0053, 65-0064
PLASTIC, 65-0045' 65-00?!
PLASTIC LINERS, 6b-0036,
65-0037' 65-0050, 65-0057,
65-0061
COSTS' 65-0036
L/U.S L^f-iCtR-l'iG, 65-U010
t^blLDlNCib' 6b-,;0bb»
bb-0147
, , 65-Ol3b
AI\L
NAL AWEAS' bb-00b(v,
65-^047
L-, CO ,T^r;EK» 6
6^-00. sb, 65-0103, 6b-0lu'j
fcD-o04B» 65-0049' bb-OUbl,
&6-OOb^' 6b-CCb3« tob-OObo,
65-OObo, 65-0062, bb-00b3,
6b-00t4, 65-OOob» 6b-00b6,
'o';-00'-,7, 6b-00o£» t>5-JUo9,
65-0129
SACKS, 6b-.vO.i7,
bb-uO- 2, 05-0070 ,
ba-0071
ST fcT CLL'-iaiMf, bb-0679
CLlMAlt Lt-FfXTf' 65-Uo36
65— vGjrJ'
65-0705
3» fca-0635' 6a-0b38
OF VLHICLE Prti image:
-------
Subject Index
65-0619. 65-0626,
_, 65-0637
6t5-a6t-6* 65-0633,
65-J634
tiVrtLUATiON* ob-0622» 6:J-06;:3
FLUSnIl.j* 6b-C!6-i5* 6a-063u
• UuHl S'.tt.PiM^. b?-C
65—1,631* 60— 0635
.vLr.R CV/U..THY,
, 65-0179, C'5-Ofciy»
» 6b-06?l. fa5-u623»
. bb~0625» b5-d62b»
i 6b-06?9» 65-0630 »
COLLECTION Ar.o DISPOSAL OF
65-U699. &5-0719
Sh'EtPEKS
SEC STREFT CLEAfgU.S, t
SYSTFMb ANALYSIS* 65-0428* 65-Ot,96
COLLECTION AIO DISPOSAL OF
CASTES'
6b-0l60r 65-0700
LEAST COST DETERMINATION*
65-0032
TAXES
SANITARY LANDFILLS* 6b-001fe
SEt ALSO COSTS
SEE INCINERATORS*
SPECIAL PURPOSE
TRAIN SYSTEM
SEE TRAhSPORTATIOl. OF WASTES
TRAINING
SFL PERSONNEL
TRAi:SFtR SYSTEMS
GENERAL DISCuSSIOli OF, 6b-0ll6»
6*5-0163* 65-0165
PARTICULAR MUNICIPALITY AND
KFGIO;.)'
65-OH3* 65-0131* 65-0208
SCOOTED, 65-C150
SPECIALISED VEHICLtS* 65-0123
TRAILER, 65-0153
TRANSPORTATION OF PASTES
BULK TRAMSPOi'T TRUCKS, 6b-0l2b
DETACHABLE cnNTAi^RS* 65-oo5t
GENERAL DISCUSSION OF, 65-oi2tf
b5-0l63, 65-0165
f'AXlWM PAYLOAD SYSTE.,* 65-013^
RAILROAD* 65-0161
ROUTES, 65-0139* 65-0.160
SHIP* 65-OlOfc* 65-014.}* 6b-0l'+t*>
216
SPECIALIZED VEHICLES* 65-0162*
b5-01&7» 65-0168
TRAIN SYSTEMS* 65-0122.
65-013^' 65-0139* 65-OlfO,
65-01^6* 65-0166
UNuERGRQUNU CONVEYORS. 65-0«t20*
65-052^
VEHICLE CLASSIFICATIONS* 65-0030
TRUCKS
CLASSIFlCATIOrg* 65-0030
CLOSED* 65-0011
COMPACTION* 65-0157* 65-0330
COSTS* 65-0032* 65-0031* 65-0035
DtlAchABLt CONTAINER, 65-0125
CF* 65-0124*
OPEKATtU* 65-01^5*
65-0152
LArvGt CAPACITY. 65-0134
'vHlNfL;/^,CE. 65-0034* 65-0035.
ob-GO<42* 00-0126' 65-015^
RENTAL* 65-uu32
&5-0321* 65-0330
65-oi4i» 65-0152
FLY, 65-0652. 65-0653* 65-C651* -
6b-0o5b* 65-0658' 6b-Q6&3»
65-0665* feb-0669' b5-0672
PRODUCT I UN IN STOKAGt
CONTAINERS* 65-0051*
65-0052, &5-UU53* 65-u36«
iNbFCTS. 65-0673
KO^E:,r, 6b-ub71
WASTE HEAT UTILIZATION
SLE INCINERATION, CENTRAL
DvATEH POLLUTION. 65-0456
AGt'lCULTUrtAL WASTES* 65-0250
COUi'!TLRCURRt ,.T EXTRACTOR*
65-0^24
i:U'iPo. 65-017S* 6b-OidS.
DISCUSSION OF*
65-OU10' 65-0426*
05-0460* 65-0462* ob-OH63»
65-0-+70, oS-04-71* 65-0494*
05-0510
CONSTITU£(iTS, 65-0410..
b5-uH24. e5-C'437' o5-045l*
65-0431
PEbTlCIOtS* b^-0423* o5-04£4*
o5-(531* 65-0532* 65-Cb3£
SAulTA;,Y LA' uFiLLS* 65-0194
65-OlcsO* 65-U183*
* 65-0423
POSTING* v
V. METHOu
65-033o,
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