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A PRESENTATION
ON
SEWAGE DISPOSAL
Presented by: Tutor:
Shrijan Basnet 163 Assist. Prof. Shukra Raj Paudel
Sibesh Kr. Singh 164 Department of Civil Engineering
Sobin Lal Pradhan 166 Pulchowk Campus, Lalitpur
Sonu Shah 167
Subash Shrestha 168
Date: 2073-03-04
Objectives:
 At the end of this presentation you will have the idea
about different methods of sewage disposal.
 You will certainly be familiar with dilution and land
disposal methods of sewage disposal.
 You will know what sewage sickness means.
Outline
6.1 Necessity and objectives of wastewater disposal
6.2 Waste water disposal methods
6.3 Wastewater disposal by Dilution process and
essential conditions for dilution
6.4 Self purification of rivers/streams
6.5 Factors affecting self purification
6.6 Oxygen sag curve
6.7 Streeter Phelps’s equation
6.8 Numericals on self purification of rivers/streams
6.9 Wastewater disposal by land treatment
6.1 Necessity and objectives of wastewater
disposal
D e f i n i t i o n :
Sewage: liquid waste from community
Removing act of sewage :: sewage disposal
N e c e s s i t y :
Accumulation causes nuisance
Selection of Pretreatment method
Protection of groundwater
O b j e c t i v e s :
To improve public health
To use sewage in farm
To protect aquatic life
6.2 Wastewater Disposal Method
Composition, Quality, Characteristic of Sewage
U
disposal
Sewage Primary Treatment
SecondaryTreatment
By Dilution
By Land
Treatment
6.3 Wastewater disposal by Dilution process
and essential conditions for dilution
Disposal into water bodies
 Purification of wastewater by self-purification of natural water
Essential Conditions :
A . Sewage
 Fresh Sewage
 No floating & suspended solids
 No toxic substances
B. Water Bodies
 High DO content
 Not being used for water supply & navigation
 Volume of water >> Volume of sewage
 Thorough mixing capacity
6.4. Self Purification of rivers/streams
Despite discharge of sewage,
Balancing its (river) DO content after few
days.
bacterial or
other
Decomposition
Organic Matter Oxygen
Nitrates,
Sulphate
Carbon
Dioxide
Stable
Byproduct
 Due to decomposition, reduction in DO content.
Deficit DO is replenished by aeration.
6.5. Factors affecting self purification
1. Dilution
 Ratio of volume of water bodies to sewage
 Higher the Dilution ratio, not appreciably reduction
in DO
C=(Cs*Qs+Cr*Qr)/(Qs+Qr)
where,
C= resulting concentration of mixture
Cs, Cr = concentration of organic content
BOD,suspended solids in sewage & river resp.
Qs, Qr =Discharges of sewage & river
2. Current
# Disperse the wastewater
# High velocity of current – reduction in time of
recovery
But affected to long length of stream.
3.Sunlight
# Enhance aquatic plants to produce oxygen
4. Sedimentation
# Removal of suspended solids by settling
# Anaerobic decomposition due to settled solids
5. Temperature
# High temp. increases solubility of oxygen in water.
# High temp. causes less self-purification time.
6. Oxidation
# Capability of stream to absorb more oxygen
7. Reduction
# Hydrolysis of organic matter
Variation of oxygen
deficit with the distance
along the stream or time
of flow from the point of
application
Oxygen deficit, D =
Saturation DO -
Actual DO
Normal saturation DO for
freshwater :
14.62 mg/l @ 0 degree
7.63 mg/l @ 20 degree
fig: OXYGEN SAG AND BOD
REMOVAL IN STREAM
6.6 Oxygen Sag Curve
Terminology:
-Initial oxygen deficit, D0
-Critical deficit , Dc
-Re-oxygenation curve, III
-De-oxygenation curve, II
-Dissolved Oxygen
fig : DEOXYGENATION,
REOXYGENATION AND OXYGEN
SAG CURVES
6.7.Streeter-Phelps Equation
 Mathematical expression for oxygen sag curve
 Concept of superposition of rate of deoxygenation &
reoxygenation
Some Formulas
Where,
Dt = DO deficit at any time t.
Lt = amount of first stage BOD remaining in the sample at
time t
K’ = BOD reaction constant (base e)
R’ = Re-Oxygenation constant (base e)
This eqn …(c) is Streeter-Phelps Equation.
Where,
Dt = DO deficit at any time t.
L0 = Ultimate BOD
K= BOD reaction constant
R = Re-Oxygenation constant
D0=Initial Do deficit @ t=0
Fig : Characteristic Oxygen Sag Curve Obtained Using
Streeter- Phelps Equation
Where,
Dc= Critical DO deficit
Tc= Time required to reach critical point
Xc= Tc * velocity of stream’v’
Put Fs = R/K (or R’/K’),
Fs is self- purification constant
Introducing ‘Fs’ in eqn (d), (e), we have
Eqn (f) is simplification of eqns (d1) & (e1).
6.8.Numericals on self purification of
rivers/streams
TYPE-1
TYPE 2
6.9 Disposal by land treatment
 It is wastewater spread on the surface of land.
Mechanism:
Some part of the wastewater evaporates;other part
percolates in the ground leaving behind suspended solids
which are partly acted upon by the bacteria and partly
oxidised by exposure to atmospheric actions of air, heat &
light.
6.9.1 Suitability of land Treatment
Alternative to river
• Not located in the vicinity
• Very small flow
Land
• Percolating land eg. Sandy , Loamy, or alluvial soil
Climate
• Arid climate
• Low watertable
• Demand for irrigation water
6.9.2. Methods of Land Treatment
Percolation Rate Method Used
 6-25 mm/min
 2-6 mm/min
 <2 mm/min
 rapid infiltration
 irrigation
 overland flow
According to the percolating capacity of soil
- Great basin or pond
is prepared where
sewage is applied and
allowed to percolate
down.
-Two or more basins
are used to maintain
adequate infiltration
capacity
-Rate of infiltration is
high(6 to 25 mm/min)Rapid Infiltration
In sewage farming, to
support plant growth,
controlled discharge
of sewage is applied
to the land
Irrigation
The controlled
discharge of
sewage is applied
on ground having a
slope 2 to 8% where
it follows down from
vegetative areas
and appears as
runoff which is
collected than
disposed off.Overland Runoff
6.9.3 Broad Irrigation & Sewage Farming
Broad Irrigation Sewage Farming
 Successful disposal of
Sewage
 Raw or settled sewage is
applied
 Suitable for relatively more
pervious soil.
 Successful growing of
the Crops
 Raw sewage isn’t used
Result: Crop is raised & Sewage is disposed by land application
6.9.4 Methods of application of sewage on Land
A. Surface Irrigation
a. Flooding Method
b. Ridge & Furrow Method
B. Subsurface irrigation
C. Spray Irrigation
A.a Flooding Method
In this method, land is divided into rectangular plots and
sewage is flooded over these plots at depth of 30 to 60 cm.
The under drains are provided to remove the percolated
effluent through soil.
A.b. Ridge & Furrow method
 Furrows are the ditches of depth 30 to 50 cm and width of
120 to 150 cm.
 Ridges have length 15 to 30m and width 120 to 250 cm.
 Furrows are filled up to 2/3 depth and on ridge crops are
grown.
B. Subsurface Irrigation
 Sewage is applied directly to root zone of the plants through
perforated pipe or pipe with open joints.
 Pipe network laid about 30 cm below the ground level. The
sewage rises up due to capillary action and utilized by plant.
C. Spray Irrigation
 Effluent sewage is spread over the land through nozzle
of pipe under pressure.
 If sufficient head available and wastewater have no any
solid matters the only it can be sprayed under pressure
through pipe fitted at tips of pipes.
6.9.5 Sewage Sickness & its Prevention
 The phenomenon of inability to take any further load of
sewage by the land.
 The pores of soil gets clogged, preventing oxidation
and causing noxious smells.
Its Prevention
• Pretreatment of Sewage
• Provision of extra land
• Under Drainage of soil
• Proper choice of land
• Rotation of crops
• Shallow depth application
References
 Punima, B.C. and Jain, Ashok, (2003), “ Waste Water
Engineering”,Laxmi Publications(P) LTD, New Delhi.
 Birdie, G.S., and Birdie, J.S., (2006), “ Water Supply
and Sanitary Engineering”, Including Environmental
Engineering Water and Air Pollution Act’s, Dhanpat
Rai Publishing Company (P) Ltd., New Delhi.
 Modi, Dr. P.N., “Sewage Treatment & Disposal &
Waste Water Engineering”, Standard Book House,
New Delhi.
 https://en.wikipedia.org/wiki/Google
Sewage Disposal

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Sewage Disposal

  • 1. A PRESENTATION ON SEWAGE DISPOSAL Presented by: Tutor: Shrijan Basnet 163 Assist. Prof. Shukra Raj Paudel Sibesh Kr. Singh 164 Department of Civil Engineering Sobin Lal Pradhan 166 Pulchowk Campus, Lalitpur Sonu Shah 167 Subash Shrestha 168 Date: 2073-03-04
  • 2. Objectives:  At the end of this presentation you will have the idea about different methods of sewage disposal.  You will certainly be familiar with dilution and land disposal methods of sewage disposal.  You will know what sewage sickness means.
  • 3. Outline 6.1 Necessity and objectives of wastewater disposal 6.2 Waste water disposal methods 6.3 Wastewater disposal by Dilution process and essential conditions for dilution 6.4 Self purification of rivers/streams 6.5 Factors affecting self purification 6.6 Oxygen sag curve 6.7 Streeter Phelps’s equation 6.8 Numericals on self purification of rivers/streams 6.9 Wastewater disposal by land treatment
  • 4. 6.1 Necessity and objectives of wastewater disposal D e f i n i t i o n : Sewage: liquid waste from community Removing act of sewage :: sewage disposal N e c e s s i t y : Accumulation causes nuisance Selection of Pretreatment method Protection of groundwater O b j e c t i v e s : To improve public health To use sewage in farm To protect aquatic life
  • 5. 6.2 Wastewater Disposal Method Composition, Quality, Characteristic of Sewage U disposal Sewage Primary Treatment SecondaryTreatment By Dilution By Land Treatment
  • 6. 6.3 Wastewater disposal by Dilution process and essential conditions for dilution Disposal into water bodies  Purification of wastewater by self-purification of natural water Essential Conditions : A . Sewage  Fresh Sewage  No floating & suspended solids  No toxic substances B. Water Bodies  High DO content  Not being used for water supply & navigation  Volume of water >> Volume of sewage  Thorough mixing capacity
  • 7. 6.4. Self Purification of rivers/streams Despite discharge of sewage, Balancing its (river) DO content after few days. bacterial or other Decomposition Organic Matter Oxygen Nitrates, Sulphate Carbon Dioxide Stable Byproduct  Due to decomposition, reduction in DO content. Deficit DO is replenished by aeration.
  • 8. 6.5. Factors affecting self purification 1. Dilution  Ratio of volume of water bodies to sewage  Higher the Dilution ratio, not appreciably reduction in DO C=(Cs*Qs+Cr*Qr)/(Qs+Qr) where, C= resulting concentration of mixture Cs, Cr = concentration of organic content BOD,suspended solids in sewage & river resp. Qs, Qr =Discharges of sewage & river
  • 9. 2. Current # Disperse the wastewater # High velocity of current – reduction in time of recovery But affected to long length of stream. 3.Sunlight # Enhance aquatic plants to produce oxygen 4. Sedimentation # Removal of suspended solids by settling # Anaerobic decomposition due to settled solids
  • 10. 5. Temperature # High temp. increases solubility of oxygen in water. # High temp. causes less self-purification time. 6. Oxidation # Capability of stream to absorb more oxygen 7. Reduction # Hydrolysis of organic matter
  • 11. Variation of oxygen deficit with the distance along the stream or time of flow from the point of application Oxygen deficit, D = Saturation DO - Actual DO Normal saturation DO for freshwater : 14.62 mg/l @ 0 degree 7.63 mg/l @ 20 degree fig: OXYGEN SAG AND BOD REMOVAL IN STREAM 6.6 Oxygen Sag Curve
  • 12. Terminology: -Initial oxygen deficit, D0 -Critical deficit , Dc -Re-oxygenation curve, III -De-oxygenation curve, II -Dissolved Oxygen fig : DEOXYGENATION, REOXYGENATION AND OXYGEN SAG CURVES
  • 13. 6.7.Streeter-Phelps Equation  Mathematical expression for oxygen sag curve  Concept of superposition of rate of deoxygenation & reoxygenation Some Formulas Where, Dt = DO deficit at any time t. Lt = amount of first stage BOD remaining in the sample at time t K’ = BOD reaction constant (base e) R’ = Re-Oxygenation constant (base e)
  • 14. This eqn …(c) is Streeter-Phelps Equation. Where, Dt = DO deficit at any time t. L0 = Ultimate BOD K= BOD reaction constant R = Re-Oxygenation constant D0=Initial Do deficit @ t=0
  • 15. Fig : Characteristic Oxygen Sag Curve Obtained Using Streeter- Phelps Equation Where, Dc= Critical DO deficit Tc= Time required to reach critical point Xc= Tc * velocity of stream’v’
  • 16. Put Fs = R/K (or R’/K’), Fs is self- purification constant Introducing ‘Fs’ in eqn (d), (e), we have Eqn (f) is simplification of eqns (d1) & (e1).
  • 17. 6.8.Numericals on self purification of rivers/streams TYPE-1
  • 18.
  • 20.
  • 21. 6.9 Disposal by land treatment  It is wastewater spread on the surface of land. Mechanism: Some part of the wastewater evaporates;other part percolates in the ground leaving behind suspended solids which are partly acted upon by the bacteria and partly oxidised by exposure to atmospheric actions of air, heat & light.
  • 22. 6.9.1 Suitability of land Treatment Alternative to river • Not located in the vicinity • Very small flow Land • Percolating land eg. Sandy , Loamy, or alluvial soil Climate • Arid climate • Low watertable • Demand for irrigation water
  • 23. 6.9.2. Methods of Land Treatment Percolation Rate Method Used  6-25 mm/min  2-6 mm/min  <2 mm/min  rapid infiltration  irrigation  overland flow According to the percolating capacity of soil
  • 24. - Great basin or pond is prepared where sewage is applied and allowed to percolate down. -Two or more basins are used to maintain adequate infiltration capacity -Rate of infiltration is high(6 to 25 mm/min)Rapid Infiltration
  • 25. In sewage farming, to support plant growth, controlled discharge of sewage is applied to the land Irrigation
  • 26. The controlled discharge of sewage is applied on ground having a slope 2 to 8% where it follows down from vegetative areas and appears as runoff which is collected than disposed off.Overland Runoff
  • 27. 6.9.3 Broad Irrigation & Sewage Farming Broad Irrigation Sewage Farming  Successful disposal of Sewage  Raw or settled sewage is applied  Suitable for relatively more pervious soil.  Successful growing of the Crops  Raw sewage isn’t used Result: Crop is raised & Sewage is disposed by land application
  • 28. 6.9.4 Methods of application of sewage on Land A. Surface Irrigation a. Flooding Method b. Ridge & Furrow Method B. Subsurface irrigation C. Spray Irrigation
  • 29. A.a Flooding Method In this method, land is divided into rectangular plots and sewage is flooded over these plots at depth of 30 to 60 cm. The under drains are provided to remove the percolated effluent through soil.
  • 30. A.b. Ridge & Furrow method  Furrows are the ditches of depth 30 to 50 cm and width of 120 to 150 cm.  Ridges have length 15 to 30m and width 120 to 250 cm.  Furrows are filled up to 2/3 depth and on ridge crops are grown.
  • 31. B. Subsurface Irrigation  Sewage is applied directly to root zone of the plants through perforated pipe or pipe with open joints.  Pipe network laid about 30 cm below the ground level. The sewage rises up due to capillary action and utilized by plant.
  • 32. C. Spray Irrigation  Effluent sewage is spread over the land through nozzle of pipe under pressure.  If sufficient head available and wastewater have no any solid matters the only it can be sprayed under pressure through pipe fitted at tips of pipes.
  • 33. 6.9.5 Sewage Sickness & its Prevention  The phenomenon of inability to take any further load of sewage by the land.  The pores of soil gets clogged, preventing oxidation and causing noxious smells. Its Prevention • Pretreatment of Sewage • Provision of extra land • Under Drainage of soil • Proper choice of land • Rotation of crops • Shallow depth application
  • 34. References  Punima, B.C. and Jain, Ashok, (2003), “ Waste Water Engineering”,Laxmi Publications(P) LTD, New Delhi.  Birdie, G.S., and Birdie, J.S., (2006), “ Water Supply and Sanitary Engineering”, Including Environmental Engineering Water and Air Pollution Act’s, Dhanpat Rai Publishing Company (P) Ltd., New Delhi.  Modi, Dr. P.N., “Sewage Treatment & Disposal & Waste Water Engineering”, Standard Book House, New Delhi.  https://en.wikipedia.org/wiki/Google