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Ocean Disposal of Wastewater
(An Introduction)
by
Prof. B. S. PANI
I. I. T. Bombay, Mumbai
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Ocean is utilized as the ultimate sink for wastewater
disposal.
The effluent (a very dilute mixture of human & otherwastes) is collected and led to a central location.
After treatment, the effluent is discharged into the ocean.
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Density of effluent is close to that of fresh water.
Due to buoyancy effects, the effluent rises to the surface and
in doing so entrains the ambient fluid and becomes very dilute.
Dilution is the solution to pollution.
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In deep stratified oceans the diluted pollutants field may
attain an equilibrium level below the ocean surface.
In shallow seas the pollutants reach the sea surface and
spreads out due to density differences that persists.
Due to wastewater treatment dilution and inactivation of
pathogens the quality of water becomes acceptable.
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Royal Commission on environmental pollution (1984) states that:
.. with well designed sewage outfalls we believe that discharge of
sewage to the sea is not only acceptable but in may cases environmentally
preferable to alternative method ofdisposal.
There is cultural feeling among some indigenous people that no
water should be polluted with human waste.
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Scarcity of land for constructing a sewage treatment plant
favors treatment of the effluent in the action.
When sewage is diluted one hundred times, it is as good asa fully treated secondary effluent.
Certainly there are good reasons for not disposing wastes
containing toxic materials and heavy metals in the ocean.
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Secondary treatment plant: The action of bacteria and other
micro-organisms in an enclosed basin help to reduce the sewage
waste.
Primary treatment: physical operations like screening and
sedimentation are used to remove floating and settable solids.
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Purification in the ocean can be to some extent controlled bysite choice, design of the diffuser, and the rate of loading. All
other processes occur naturally following discharge of effluent.
In contrast, the purification in a treatment plant is closely
controlled.
Concentration of a pollutant =mixtureofVolume
pollutantofMass,ppm etc.
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The local environmental impact is increased by the concentration
Dilution =aC(C
)a
Co
(C
Where, Co & Ca = effluents and ambient concentration respectively.
Initial dilution S= Minimum dilution achieved where the mixed
effluent reaches the water surface or trapping level, at a distance of
the orders of the water depth downstream. Initial dilution is water the
control of the engineer.
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In still water S=f(Fr, H/D,o) and is independent of Reynoldsnumber (inertia/ viscous force) exceeding 2000.
Densimetric Froude number =
gd
u
ao
o
For jets Fr
For plumes Fr 1
For most outfalls the Fr lies between 4 to 18 and the flow can be
classified as Buoyant jets.
= Inertia/ buoyancy
force per unit mass
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The velocity and concentration distributions are nearly Gaussian
The initial volume and specific momentum fluxes for a circular
jet are
o2 uD
4
oQ
2o
2o UD
4
M
Average dilution for a round jet
1o
21
o QM0.29oQQS x
Average dilution for a round plume
1oQzoF0.163S
35
31
(Specific momentum)
Where the initial buoyancy flux ga
ud4
oF o2
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Example: Estimate the average dilution for uo=1.2m/s, D=0.15m, H=15m
When the outfall discharges into
a) a fresh water lake
b) the ocean with relative density difference of 0.02
Solution:/s3m210x2.121.2x20.15x
4oQ
2/s4m210x2.5421.2x20.15x4
oM
In fresh water
32.712)10x(2.12x15x2
1)210x(2.54x0.29S
In the ocean:310x4.169.81x0.02x1.2x20.15x
4
oF
1131)210x(2.1235
1531)310x(4.160.163S
u
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In the presence of buoyancy, dilution is
enhanced.
Cross flow of ambient helps to dilute the
effluent in a significance way.
Eq. Shape & Moore(1987)
Say,
Thus, a four fold increase in dilution takes place
1.33o
0.359
o
aoM S)u
u1.57(SS
1.0,100 o
a
o
u
uS
0.1uu100,S
o
ao
414100x1.59(0.1)100S 1.330.359M
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THANK YOU