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Sewage.:- Is a term used to describe human body waste,
normally defined as "Black Water". This is the only liquid that is
treated with a "Marine Sanitation Device"
Grey Water:-
Is defined as water from baths, showers, wash basins, sinks,
laundries etc. At present there is no
requirement for treatment of Grey Water prior to its discharge overboard.
Terms used in waste treatment
Biological Oxygen Demand (B.O.D.)
Is used to give a measure of the
strength of sewage, it identifies the biologically decomposable substances and
is a test that depends on the activity of bacteria, which in the presence of
oxygen feed on and consume organic matter.
Results of the test are expressed as
the amount of oxygen taken by a one litre sample (diluted with aerated water)
when incubated at 20o for five days. Can be defined as the amount of
oxygen utilised by micro-organisms in the stabilisation of organic matter,
B.O.D. of raw sewage is 300 to 600
mg/litre
I.M.O. recommend a B.O.B. of 50
mg/litre after treatment.
Coliform Count:-
Coliform organisms are recognised as
the Indicator Organisms of sewage pollution. The numbers present in
sewage are large each person contributing between 125 billion in winter to 400
billion in summer.
Coliform are present in the human
intestine and their presence in water is taken as an indication of the Pathogen
count.
The Pathogens are disease causing
organisms responsible
for Typhoid, Dysentery, Poliomyelitis, Cholera etc.
I.M.O. recommend a coliform count of
250/100 ml. of effluent after treatment.
Solids:-
Dissolved:- Solids which are in
solution.
Suspended:- Solids physically
suspended in sewage that can be removed by
laboratory filtration. Are
relatively high in organic matter.
Settleable:- Suspended solids that
will subside in quiescent liquid in a
reasonable period (usually taken
as one hour)
The Suspended Solids level of raw
sewage is 300 to 400 mg./litre.
I.M.O. recommend a level, after
treatment of 50 mg./litre.
Glossary cont'd/
Residual Disinfectant:-
After treatment the residual
disinfectant should be as low as possible.
Canadian restriction is between 0.5
and 1.0 mg./litre.
I.M.O. prefer the use of
Ultra-Violet exposure to Chlorination.
Biological Digestion Of Sewage
Anaerobic Process:- Anaerobic bacteria can only
multiply in the absence of free oxygen, they use chemically bound oxygen to
survive.
In the anaerobic process the
bacteria break down the organic matter into, water, carbon dioxide, methane,
hydrogen sulphide and ammonia.
The process is also called
Putrefaction. The gasses produced are both noxious and toxic. The effluent
produced is of poor quality and other by-products are highly corrosive.
Aerobic Process:- Aerobic bacteria require free
oxygen to survive. In the aerobic process the bacteria break down the organic
matter safely.
The Aerobic Process has end products
of :-
H2.O + C.O2 + Inert
Residue + Energy To Synthesise New Bacteria
Note!
Disposal of waste from ships was
discussed internationally as long ago as 1973, but there was little initial
progress on legislation. This led to certain countries introducing legislation
unilaterally, among these were Canada, Japan, Sweden, U.S.S.R. and U.S.A. all
with their own variations.
Other nations have since followed,
but the variation between different countries still causes confusion for
visiting ships.
Treatment plants can be broadly
divided into:-
Physical Processes:- Comminutation, Filtration, Ultrasonic
Degradation and Incineration.
Chemical Processes.
Biological Processes:- Degradation
by micro-organisms. BIOLOGICAL
TREATMENT SYSTEM
The
principle used involves "Activated Sludge" and has been used ashore
for many years. Raw sewage is introduced into an aeration chamber, where
"Biolysis" of the faecal matter is achieved by micro-organisms in the
presence of free oxygen.
After
vigorous agitation the liquor is transferred to the settlement hopper, where
activated sludge falls to the bottom.
The
process results in a light brown precipitate, that settles, leaving a clear
odourless liquid.
Periodically
some of the sludge is returned to the aeration chamber to help maintain the
biolysis.
Liquid
effluent overflows into the contact tank, where it is usually diluted with
"Grey
Water"
before its eventual discharge overboard.
The
operation is never as successful on board ship as it is ashore. mainly because
of variations in load and the effect of sea water. The main disadvantage of
this plant is that micro-organisms developed in salt water may die off in fresh
water, during the time required to develop new organisms the discharge effluent
level will be high.
After a
shut down it may take up to five days until the growth of new organisms is
sufficiently developed to maintain the low effluent levels required.
Also
heavily chlorinated water is a danger to marine life, hence there is a problem
with residual disinfectant, Canada is particularly strict on this, mainly as a
protection for the great lakes.
Either"Sodium
Hyperchlorate" or Calcium Hyperchlorate is used for chlorination.
NOTE!:
If
sewage is not adequately oxygenated, putrefaction sets in. Anaerobic bacteria
multiply and produce Urea, Ammonia, Hydrogen Sulphide, and Methane. From this it is clear that if
sewage is not inactivated and is stored for more than a few hours it MUST be
thoroughly aerated.
A
typical plant gives:-
B.O.D. < 40 mg/litre
Suspended Solids < 50 mg/litre
Coliform < 200 per 100 ml.
It is
due to the difficulties with the activated sludge type at sea, that many owners
stick with the physical/chemical types of treatment.
Many systems in use at sea are
of the aerobic type, where the bacteria generated require a feed of oxygen to
thrive. Raw sewage enters the first stage (aeration) chamber where it is broken
down by micro-organisms, with the products being water, carbon dioxide and an
inert residue. Note in the absence of oxygen, due perhaps to a restriction to
the oxygen supply, anaerobic bacteria thrive and the products
include hydrogen sulphide and methane, which are flammable and poisonous, see
MGN 33.
The tank is sized for the ship to give a dwell time in normal use of
about 24 hours. The liquor is then transferred to the settlement hopper, where
precipitation takes place leaving a clear colourless liquid, and bacteria rich
"activated sludge" at the bottom of the hopper. This sludge is
periodically returned to the first stage to help maintain the bacteria colony.
The liquid effluent overflows,
via a chlorination unit, into a third stage tank where it is diluted with
"Grey Water" (drains from sinks, baths etc.). A float operated pump
periodically discharges the third stage tank overboard.
A macerator may sometimes be
fitted to the sewage (black water) inlet to the first stage, and some
authorities prefer the use of Ultra Violet fight to kill off bacteria in the
third stage, rather than chlorine which can damage marine life.
The maintenance for these
plants generally consists of regularly removing the sludge build up,
maintaining clear passageways (including ventilation) and pump and compressor
overhauls. The plant should also be inspected internally on an annual basis and
any coatings reapplied.
When working on the plant
regard to the risks is paramount. Risks include the fact that it is an enclosed
space, possible presence of anaerobic conditions and biological hazard from
waste products – including hospital drains.
THE AEROBIC PROCESS
Aerobic bacteria
require free oxygen to survive, and break down the organic matter to
H2O + CO2 + Inert Residue
Anaerobic bacteria
produce toxic and flammable gasses in a process known as putrefaction, the
products being H2O
+ CO2 + H2S + CH4 ( Methane )
BIOCHEMICAL OXYGEN DEMAND (B.O.D.)
Gives a measure of the strength
of sewage, since if oxygen is being used then there are still bacteria present
and they are still actively digesting the sewage. The test expresses the amount
of oxygen taken by a one litre sample incubated at 20°C for five days. The B.O.D. of raw sewage is 300‑600
mg/litre. IMO recommend 50mg/litre after treatment
COLIFORM COUNT
Coliform Bacteria are present
in the human intestine and their presence in sewage is an indicator of the
level of pollution. They indicate the presence of pathogens which may cause
Typhoid, Dysentery etc.
Each person contributes 125 to
400 billion bacteria per day, IMO recommend a count of 250/100 ml of treated
sewage.
SUSPENDED SOLIDS
These are solids which are
physically suspended in solution. They can be removed by filtration through an
asbestos mat, which is then dried and weighed Level in Raw Sewage is 300‑400
mg/litre. IMO recommend a final level of 50 mg/litre
RESIDUAL DISINFECTANT
Should be as low as possible
after final treatment ‑ Canadian restriction is between 0.5 to 1.0 mg/litre IMO
prefer Ultra‑Violet exposure to chlorination
MGN33
When not equipped with active
aeration features, sewage tanks should be emptied and flushed through every 24
hours unless some treatment is used which maintains satisfactory conditions
When active aeration features
are fitted, manufacturers' recommendations with respect to air blowers,
distribution systems etc. should be followed and the plant maintained annually
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