Encyclopedia of Environmental Science and Engineering, Volume I and II

(Ben Green) #1
Collection

Collection cost has been estimated to represent about 80% of
the total cost of collection and disposal by sanitary landfi ll
and 60% when incineration is used. In 1968 collection cost
alone was found to average 10 to 13 dollars per ton.
The frequency of collection will depend upon the quan-
tity of solid waste, time of the year, socio-economic status
of area served, and municipal or contractor responsibility. In
business districts refuse, including garbage from hotel and
restaurants, should be collected daily except Sundays. In res-
idential areas, twice a week refuse collection during warm
months of the year and once a week at other times should
be the maximum permissible interval. Slum and ghetto areas
usually require at least twice a week collection. The recep-
tacle should be either emptied directly into the garbage truck
or carted away and replaced with a clean container. Refuse
transferred from can to can will invariably cause spilling,
with resultant pollution of the ground and attraction of rats
and fl ies. If other than curb pick-up is provided, the cost of
collection will be high. Some property owners are willing to
pay for this extra service.

Transfer Station

The urban areas around cities have been spreading leaving
fewer nearby acceptable solid waste disposal sites. This has
generally made necessary the construction of incinerators in
cities or on the outskirts, or the transportation of wastes longer
distances to new sites. However, as the distance from the cen-
ters of solid waste generation increases, the cost of direct haul
to a site increases. A distance is reached (in terms of time)
when it becomes less expensive to construct an incinerator,
or a transfer station near the center of solid waste generation
where wastes from collection vehicles can be transferred to
large tractor-trailers for haul to more distant disposal sites.
Rail haul and barging to sea also involve the use of
transfer stations. They may include one or a combination of
grinding, compaction to various densities, and baling.

Treatment and Disposal of Solid Wastes

Solid waste treatment and disposal methods include the open
dump, hog feeding, incineration, grinding, and discharge to
a sewer, milling, compaction, sanitary landfi ll, dumping,
and burial at sea, reduction, composting, pyrolization, wet
oxidation, and anaerobic digestion. The common acceptable
methods are incineration, sanitary landfi ll and in some part
of the world composting.
Open Dump The open dump is all too common and needs
no explanation. It is never satisfactory as usually main-
tained. Refuse is generally spread over a large area provid-
ing a source of food and harborage for rats, fl ies, and other
vermin. It is unsightly, an odor and smoke nuisance, a fi re
hazard, and often a cause of water pollution. It should be
eliminated or its operation changed to a sanitary landfi ll.
Hog Feeding Where garbage is fed to hogs, careful susper-
vision is necessary. The spread of trichinosis in man, hog

cholera, the virus of foot-and-mouth disease, and vesicular
exanthema in swine is encouraged when uncooked garbage
is fed to hogs. In some instances, tuberculosis, swine ery-
sipelas, and stomatitis may also be spread by raw garbage.
The boiling for thirty minutes of all garbage fed to hogs will
prevent transmission of trichinosis and economic loss of the
swine industry due to hog illness and death.
Grinding The grinding of garbage is fast becoming a common
method of garbage disposal. It is highly recommended from a
convenience and public health standpoint, but the disposal of
other refuse remains to be handled. The putrescible matter is
promptly removed thereby eliminating this as a source of odors
and food for rats, fl ies, and other vermin. In one system, the
home grinder is connected to the kitchen sink drain. Garbage
is shredded into small particles while being mixed with water
and is discharged to the house sewer. In another system, gar-
bage is collected as before but dumped into large, centrally
located garbage grinding stations that discharge garbage to the
municipal sewerage system. In small communities, the gar-
bage grinding station may be located at the sewage-treatment
plant. The strength of the sewage is increased and additional
sludge digestion and drying facilities will be required when a
large amount of garbage is handled.
Disposal at Sea Where dumping at sea is practiced, all gar-
bage and other refuse is dumped into large garbage scows or
barges. The scows are towed by tugs and the garbage is taken
out to sea and dumped a suffi cient distance out to prevent the
refuse being carried back to shore and causing a nuisance.
Bad weather conditions hamper this operation and unless
this method is kept under very careful surveillance, abuses
and failures will result. Because of the cost of maintaining a
small navy and diffi culties in satisfactorily carrying out this
operation, coastal cities have reverted to sanitary landfi ll and
incineration. In recent years, consideration has been given
to the compaction of refuse to a density greater than 66.5
pounds per cubic foot prior to transport and then disposal
by burial in the ocean at depths greater than 100 feet, based
upon oceanographic conditions, to ensure there will be no
mixing with surface water. More research is needed to deter-
mine stability of the compacted refuse and effect on marine
life. See High density compaction.
Garbage Reduction In the reduction method of garbage
disposal, the garbage is cooked under pressure. Fats melt
out and are separated from the remaining material. The fat
is used in the manufacture of soaps or glycerines and the
residue is dried, ground, and sold for fertilizer or cattle feed.
Odor complaints are associated with this process and, where
a solvent such as naphtha is used to increase the extraction
of fat, a greater fi re hazard exists. The use of synthetic deter-
gents and chemical fertilizers and high operating costs have
led to the abandonment of this process.
Composting Composting is the controlled decay of organic
matter in a warm, moist environment by the action of bacte-
ria, fungi, molds, and other organisms. This may be an aero-
bic and/or anaerobic operation. Moisture is maintained at
40–65%, 50–60% is best. Composition of the refuse, disposal
of refuse not composted, demand for compost and salvaged
material, odor production and control, public acceptance and

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