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ENVIRONMENTAL ENGINEERING –II
Course Learning Objectives:
The objective of this course is:
• Outline planning and the design of wastewater collection, conveyance and treatment systems for a
community/town/city
• Provide knowledge of characterisation of wastewater generated in a community
• Impart understanding of treatment of sewage and the need for its treatment.
• Summarize the appurtenance in sewerage systems and their necessity
• Teach planning, and design of septic tank and imhoff tank and the disposal of the effluent from these
low cost treatment systems
• Effluent disposal method and realise the importance of regulations in the disposal of effluents in
rivers
Course Outcomes:
By the end of successful completion of this course, the students will be able to:
• Plan and design the sewerage systems
• Select the appropriate appurtenances in the sewerage systems
• Analyze sewage and suggest and design suitable treatment system for sewage treatment
• Identify the critical point of pollution in a river for a specific amount of pollutant disposal into the
river
• Suggest a suitable disposal method with respect to effluent standards.
SYLLABUS:
UNIT – I: Introduction to Sanitation – Systems of sanitation – relative merits & demerits – collection
and conveyance of waste water – sewerage – classification of sewerage systems- Estimation of sewage
flow and storm water drainage – fluctuations – types of sewers - Hydraulics of sewers and storm drains–
design of sewers – appurtenances in sewerage – cleaning and ventilation of sewers
UNIT – II: Pumping of wastewater: Pumping stations – location – components– types of pumps and
their suitability with regard to wastewaters.
House Plumbing: Systems of plumbing-sanitary fittings and other accessories– one pipe and two pipe
systems – Design of building drainage
UNIT – III: Sewage characteristics – Sampling and analysis of wastewater - Physical, Chemical and
Biological Examination-Measurement of BOD and COD - BOD equations
Treatment of sewage: Primary treatment-Screens-grit chambers-grease traps– floatation– sedimentation –
design of preliminary and primary treatment units.
UNIT – IV: Secondary treatment: Aerobic and anaerobic treatment process comparison.
Suspended growth process: Activated Sludge Process, principles, designs, and operational problems,
modifications of Activated Sludge Processes, Oxidation ponds, Aerated Lagoons.
Attached Growth Process: Trickling Filters–mechanism of impurities removal- classification– Design-
operation and maintenance problems. RBCs, Fluidized bed reactors
UNIT V: Miscellaneous Treatment Methods: Nitrification and Denitrification – Removal of Phosphates
–UASB–Membrane reactors-Integrated fixed film reactors. Anaerobic Processes: Septic Tanks and
Imhoff tanks- working Principles and Design–Reuse and disposal of septic tank effluent, FAB Reactors.
UNIT – VI: Bio-solids (Sludge) management: Characteristics-SVI, handling and treatment of sludge-
thickening – anaerobic digestion of sludge, Sludge Drying Beds. Centrifuge.
Disposal of sewage: Methods of disposal – disposal into water bodies-Oxygen
Sag Curve-Disposal into sea, disposal on land- sewage sickness.
Text Books
1. Wastewater Engineering Treatment and Reuse, Metcalf & Eddy, Tata McGraw-Hill edition.
2. Industrial Water and Wastewater Management, K.V.S.G. Murali Krishna.
3. Elements of Environmental Engineering, K. N. Duggal, S. Chand & Company Ltd. New Delhi, 2012.
Introduction to Sanitation
UNIT – I
Garbage:
It is a dry refuse which includes, waste papers, sweepings from streets and markets, vegetable peelings
etc. The quantity of garbage per head per day amounts to be about .14 to .24 kg for Indian conditions.
Garbage contains large amount of organic and putrefying matter and therefore should be removed as
quickly as possible.
Refuse:
This is the most general term to indicate the wastes which include all the rejects left as worthless, sewage,
sullage – all these terms are included in this term.
Rubbish:
It consists of sundry solid wastes from the residencies, offices and other buildings. Broken furniture,
paper, rags etc., Are included in this term. It is generally dry and combustible.
Sullage:
It is the discharge from the bath rooms, kitchens, wash basins etc., It does not include discharge from the
lavatories , hospitals , operation theaters , slaughter houses which has a high organic matter .
Sewage :
It is a dilute mixture of the wastes of various types from the residential, public and industrial places . It
includes sullage water and foul discharge from the water closets, urinals, hospitals, stables ,etc.
Invert:
It is the lowest point of the interior of the sewer at any c/s.
Sludge:
It is the organic matter deposited in the sedimentation tank during treatment.
Storm water :
It is the surface runoff obtained during and after the rainfall which enters sewers through inlet. Storm
water is not foul as sewage and hence it can be carried in the open drains and can be disposed off in the
natural rivers without any difficulty.
Sanitary sewage :
It is the sewage obtained from the residential buildings & industrial effluents establishments‘. Being
extremely foul it should be carried through underground conduits.
Bacteria:
These are the microscopic organisms. The following are the groups of bacteria:
Aerobic bacteria: they require oxygen &light for their survival.
Anaerobic bacteria: they do not require free oxygen and light for survival.
Facultative bacteria: they can exist in the presence or absence of oxygen. They grow more in absence
of air.
Domestic sewage:
It is the sewage obtained from the lavatory basins, urinals &water closets of houses, offices &
institutions. It is highly foul on account of night soil and urine contained in it. Night soil starts
putrefying & gives offensive smell. It may contain large amount of bacteria due to the excremental
wastes of patients. This sewage requires great handling &disposal.
Industrial sewage:
It consists of spent water from industries and commercial areas. The degree of foulness depends on
the nature of the industry concerned and processes involved.
Sewers:
Ewers are underground pipes which carry the sewage to a point of disposal.
Sewerage:
The entire system of collecting, carrying &disposal of sewage through sewers is known as sewerage.
Dry weather flow (DWF):
Domestic sewage and industrial sewage collectively, is called as DWF. It does not contain storm
water. It indicates the normal flow during dry season.
Different Methods of domestic waste water disposal include (Systems of Sanitation)
1. Conservancy system
2. Water carriage system
Conservancy system
Sometimes the system is also called as dry system. This is out of date system but is prevailing in small
towns and villages. Various types of refuse and storm water are collected conveyed and disposed of
separately. Garbage is collected in dustbins placed along the roads from where it is conveyed by trucks
ones or twice a day to the point of disposal. all the non combustible portion of garbage such as sand dust
clay etc., are used for filling the low level areas to reclaim land for the future development of the town.
The combustible portion of the garbage is burnt. The decaying matters are dried and disposed of by
burning or the manufacture of manure.
Water carriage system
With development and advancement of the cities urgent need was felt to replace conservancy system
with some more improved type of system in which human agency should not be used for the collection
and conveyance of sewage .After large number of experiments it was found that the water is the only
cheapest substance which can be easily used for the collection and conveyance of sewage. As in this
system water is the main substance therefore it is called as water carriage system.
Relative Merits & Demerits of Sanitation
Merits
• the fundamental principles of sanitation of the community is to remove all decomposable matter, solid
waste, liquid or gaseous away from the premises of dwellings as fast as possible after it is produced, to
a safe place , without causing any nuisance and dispose it in a suitable manner so as to make it
permanently harmless.
Demerits
• If proper arrangements for the collection, treatment and disposal are not made, they will go on
accumulating and create foul condition.
• If untreated water is accumulating, the decomposition of the organic materials it contains can lead to
the production of large quantity of mal odorous gases.
• It also contains nutrients, which can stimulate the growth of aquatic plants and it may contain toxic
compounds.
Classification of Sewerage Systems
1. Separate system of sewage
2. Combined system of sewage
3. Partially combined or partially separate system
Separate system of sewerage
In this system two sets of sewers are laid .The sanitary sewage is carried
through sanitary sewers while the storm sewage is carried through storm
sewers. The sewage is carried to the treatment plant and storm water is
disposed of to the river.
Combined system of sewage
When only one set of sewers are used to carry both sanitary sewage and
surface water. This system is called combined system.
Sewage and storm water both are carried to the treatment plant through
combined sewers
Partially combined or partially separate system
A portion of storm water during rain is allowed to enter sanitary sewer to
treatment plants while the remaining storm water is carried through open
drains to the point of disposal.
Estimation of sewage flow
Sanitary sewage is mostly the spent water of the community into sewer system with some groundwater
and a fraction of the storm runoff from the area, draining into it. Before designing the sewerage system, it
is essential to know the quantity of sewage that will flow through the sewer.
The sewage may be classified under two heads:
1. The sanitary sewage, and
2. Storm water
Sanitary sewage is also called as the Dry Weather Flow (D.W.F), which includes the domestic sewage
obtained from residential and residential and industrials etc., and the industrial sewage or trade waste
coming from manufacturing units and other concerns.
Storm water consists of runoff available from roots, yards and open spaces during
rainfall.
Quantity of Sewage
It is usual to assume that the rate of sewage flow, including a moderate allowance for infiltration equals to
average rate of water consumption which is 135 litre/ head /day according to Indian Standards. It
varies widely depending on size of the town etc. this quantity is known as Dry Weather Flow (D.W.F). It
is the quantity of water that flows through sewer in dry weather when no storm water is in the sewer.
Rate of flow varies throughout 24 hours and is usually the greatest in the fore-noon and very small from
midnight to early morning. For determining the size of sewer, the maximum flow should be taken as
3 * D.W.F.
Design Discharge of Sanitary Sewage
The total quantity of sewage generated per day is estimated as product of forecasted population
at the end of design period considering per capita sewage generation and appropriate peak factor. The per
capita sewage generation can be considered as 75 to 80% of the per capita water supplied per day.
Factors affecting the quantity of sewage flow
1. Population
2. Type of area
3. Rate of water supply
4. Infiltration and exfiltration
Design Period
The future period for which the provision is made in designing the capacities of the various components
of the sewerage scheme is known as the design period.
The design period depends upon the following:
1. Ease and difficulty in expansion
2. Amount and availability of investment
3. Anticipated rate of population growth, including shifts in communities, industries and commercial
investments
4. Hydraulic constraints of the systems designed
5. Life of the material and equipment
Fluctuations in sewage flow
The sewage flow, like the water supply flow, is not constant in practice but varies. The fluctuation may, in
a similar way, be seasonal or monthly, daily and hourly.
Variation occurs in the flow of sewage over annual average daily flow. Fluctuation in flow occurs from
hour to hour and from season to season. The typical hourly variation in the sewage flow is shown in the
Figure.
The first peak flow generally occurs
in the late morning it is usually about
200 percent of the average flow while
the second peak flow generally
occurs in the early evening between 6
and 9p.m. and the minimum flow
occurring during the night after
twelve or early hours of the morning
is generally about half of the average
flow.
Due to variation in discharge, the depth of flow varies, and hence the hydraulic mean depth (r) varies.
Due to the change in the hydraulic mean depth, the flow velocity (which depends directly on r2/3) gets
affected from time to time. It is necessary to check the sewer for maintaining a minimum velocity of
about 0.45 m/s at the time of minimum flow (assumed to be 1/3rd of average flow). The designer should
also ensure that a velocity of 0.9 m/s is developed at least at the time of maximum flow and preferably
during the average flow periods also. Moreover, care should be taken to see that at the time of maximum
flow, the velocity generated does not exceed the scouring value.
Quantity of storm water flow
When rain falls over the ground surface, a part of it percolates into the ground, a part is evaporated in the
atmosphere and the remaining part overflows as storm water. This quantity of storm water is very large as
compared with sanitary sewage.
Factors affecting storm water
The following are factors which affect the quantity of storm water:
1. Rainfall intensity and duration.
2. Area of the catchment.
3. Slope and shape of the catchment area.
4. Nature of the soil and the degree of porosity.
5. Initial state of the catchment.
Estimate of quantity of storm water
Generally there are two methods by which the quantity of storm water is calculated:
1. Rational method
2. Empirical formulae method
Rational method
Runoff from an area can be determined by the Rational Method. The method gives a reasonable estimate
up to a maximum area of 50 ha (0.5 Km2).
Where,
Q= quantity of storm water in m3/sec
C= coefficient of runoff
i= intensity of rainfall
A= area of drainage in hectare
the value of runoff coefficient, C is varies from 0.01 for forest or wooded area to 0.95 for a water tight
roof surfaces.
Runoff coefficient (overall) C =
Where:
A1, A2 ,A3….are different types of area and
C1, C2, C3…..are their runoff coefficient respectively.
Empirical formula method
For determining the runoff from very large areas, generally empirical formulae are used. All the empirical
formulae are applicable only under certain specific conditions such as slope of land, imperviousness, rate
of rainfall etc.
Time of concentration
The time taken for the maximum runoff rate to develop, is known as the time of concentration, and is
equal to the time required for a drop of water to run from the farthest point of the watershed to the point
for which the runoff is to be calculated.
The time of concentration refers to the time at which the whole area just contributes runoff to a point.
Tc= te+tf
Where,
tc = time of concentration
te = time of entry to the inlet (usually taken as 5 – 10 min)
tf = time of flow in the sewer
Time of concentration is made up of inlet time (over land flow) and channel flow time.
Time of entry (inlet time or overland flow): is the time required for water to reach a defined channel such
as a street gutter, plus the gutter flow time to the inlet.
Channel flow time: is the time of flow through the sewers to the point at which rate of flow is being
assessed.
For application of the rational method, TxDOT recommends that tc be less than 300 minutes (5 hours)
and greater than 10 minutes.
Morgali and Linsley Method
For small urban areas with drainage areas less than ten or
twenty acres, and for which the drainage is basically
planar, the method developed by Morgali and Linsley
(1965) is useful. It is expressed as
where:
tc = time of concentration (min),
i = design rainfall intensity (in/hr),
n = Manning surface roughness
(dimensionless),
L = length of flow (ft), and
S = slope of flow (dimensionless).
Kirpich Method
For small drainage basins that are dominated by channel flow, the Kirpich (1940) equation can be used.
The Kirpich equation is
tc = 0.0078(L3/h)0.385
where:
tc = time of concentration (min),
L = length of main channel (ft)
h = relief along main channel (ft).
The Kirpich method is limited to watershed with a drainage area of about 200 acres.
Kerby-Hatheway Method
For small watersheds where overland flow is an important component, but the assumptions inherent in the
Morgali and Linsley approach are not appropriate, then the Kerby (1959) method can be used. The Kerby-
Hatheway equation is
tc = (0.67NL/√S)0.467
where:
tc = time of concentration (min),
N = Kerby roughness parameter (dimensionless)
S = overland flow slope (dimensionless).
Types of sewer according to material
1. Asbestos Cement (AC) Sewer
2. Brick Sewer
3. Cement Sewer
4. Cast iron (CT) Sewer
5. Steel Sewers
6. Plastic Sewers
Types of sewer according to shapes
Sewers are generally circular pipes laid below ground level, slopping continuously towards the outfall.
These are designed to flow under gravity. Mostly sewers of circular shape are used in all the sewerage
schemes, because of the following facts:
• It affords least perimeter and hence construction material required is minimum.
• They are easy to construct and handle.
• Since it has no corners, there are less chances of deposition of organic matters.
• They possess excellent hydraulic properties.
However, sewers of non circular shapes are used for the following reasons.
• To develop self cleansing velocity in the sewer, when the flow is minimum.
• To effect economy in the construction.
• To increase the headway so that a man can enter easily for repairs, and cleaning.
Following are the non-circular shapes of sewers which are commonly used for sewers:
New/ Modified Egg shaped Sewer
Box or rectangular sewers
Basket-Handle Section
Horse shoe sewer section
U-shaped section
Semi-circular Section
Semi-elliptical section
Parabolic section
Self cleansing velocity
It is necessary to maintain a minimum velocity in a sewer line to ensure that suspended
solids do not deposit and cause choking troubles. Such a minimum velocity is called as self cleansing
velocity. Self cleansing velocity is determined by considering the particle size and specific weight of the
suspended solids in sewage.
The velocity which can cause automatic self cleansing can be found out by the following formula given
by Shield:
V = √ [(8K/f) ((SS-S)/S) g d]
Where:
f = Darcy‘s co-efficient of friction,0.03
K = characteristics of solid particles
= 0.06 for organic and
= 0.04 for inorganic solids
SS = specific gravity of particles
= 2.65 for inorganic and
= 1.2 for organic solids
S = specific gravity of sewage, 1.0
G = acceleration due to gravity
D = diameter of particle
Hydraulics of sewers and storm drains
Dia. of sewers in
mm
Self cleansing velocity in
m/sec
150-300 1.0
300-600 0.75
>600 0.6
As per Badmin Lathom's recommendations
Empirical formulae used in design of sewers
Chezy‘s formula: V = C √R.S (or) C √mi
Where,
V = velocity of flow in m/sec
R = hydraulic mean depth in m
S = slope of the sewer = Fall of sewer/length
C = Chezy‘s contact.
Kutter‘s formula for Chezy‘s contact is given by:
C =
[23 + (0.00155/S) + (1/n)]
[ 1 + (23 + (0.00155/S))(n/√R) ]
Where,
n = coefficient of roughness or rughosity factor
Manning‘s formula: V = (1/n) R2/3 S1/2
Crimp‘s and Burge‘s formula: V = 83.33 R2/3 S1/2
Hazen –Williams formula: V = 0.85 C R0.6 S0.54
the value of C varies depending upon the surfaces.
S no. Material of sewer Value of
n
1.
Brick sewers
a) Flush pointed 0.015
b) Plastered smooth 0.013
2. Stoneware sewers 0.014
3. Cast iron 0.013
4.
Smooth earthen
channel
0.020
5. Rough channel 0.030
S no. Type of material Value of C
1
Stoneware pipes in good
condition
110
2 New cast iron 130
3 Very smooth surfaces 140
Hydraulic Characteristics of Circular Sewer Running Full or Partially Full
Hydraulic Mean Depth, R(or)m = A/P
Solving for half full sewer, R(or)m = D/4
Non-scouring velocity
The permissible maximum velocity to prevent eroding is termed
as non- scouring velocity and it should be limited to 3.0 m/s.
Design of sewers
Testing of sewer line
It is necessary to test the sewer after its laying for water tightness before backfilling of the excavted earth.
Smoke test: This test is performed for soil pipes, vent pipes laid above ground. The test is conducted
under a pressure of 2.5m of water and maintained for 15 minutes after all trap real
have been filled with water. The smoke is produced by burning oil waste or tar paper in combustion
chamber of a smoke machine.
Water test: This test is performed for underground sewer pipes before back filling is done. The test
should be carried out by suitably plugging the lower end of the drain and filling the system with water. A
knuckle band shall be temporarily jointed at the top end and a sufficient length of vertical pipe is jointed
so as to provide the required test head.
Subsidence of test water may be due to
Absorption by pipes and joints
Leakages at joints etc.
Any leakage if visible and defective part of work if any should be made good.
Test for straightness and obstruction: For this test, a mirror is placed in front of one end of sewer and
the image of the section is observed. If the sewer line is straight, the image should be circular. If it is not a
complete circle, then it is not straight. For testing for obstruction, by inserting a steel call at upper end and
if there is no obstruction in the sewer line, the call will emerge out from the lower end.
Sewer Appurtenances
Proper functioning and to facilitate maintenance of the sewage system, various additional
structures have to be constructed on the sewer lines. These structures are known as sewer
appurtenances.
Following are the important appurtenances.
1.Manholes
2.Inlets
3.Catch basins
Manholes
The manholes are R.C.C or masonry chambers
constructed on the sewer line to facilitate a
man to enter the sewer line and make the
necessary inspection and repairs. These are
fitted with suitable cast iron covers. The
manholes should be installed at every points
where there is a change in direction, change in
pipe size, or considerable change in gradient.
4.Flushing devices
5.Regulators
6.Inverted siphons
7.Grease and oil traps
8.Lamp holes
9.Leaping weirs
10.Junction chambers
Inlets
These are meant to admit the surface runoff
to the sewers and form a very important part
of the system. Their location and design
should therefore be given careful
consideration.
Catch Basins
Catch basins are the structures of pucker chamber
and a stout cover. They are meant for the
retention of suspended grit, sludge and other
heavy debris and floating rubbish from rain water
which otherwise might have entered and cause
choking problems.
Flushing devices
Flushing tanks are provided to flush the sewers. They
are seldom used. At such places where self cleansing
velocity is not developed or when the ground is flat and
it is not possible to lay the sewer lines at designed
gradients, flushing tanks required to flush the sewer
line.
Grease and Oil traps
The sewage from kitchens of hotels and
restaurants and industries contains oil and
grease and fats. If these oils and greases are
not removed from the sewage they will stick
to the interior surface of the sewer and
clogging.
Regulators
A Regulator is a device that diverts
sewage flow from one sewer into
another. The regulator usually goes
into action when the sewage flow
reaches a predetermined amount. It
may then divert all the sewage or only
that part above the predetermined flow
at which it begins to function.
Regulators are mostly used where
combined sewers discharge into
interceptors.
Inverted siphons
The true siphon is a sewer that runs full having its flow line above the hydraulic grade line. The
pressure in the sewer line will be greater than atmospheric pressure. On the other hand inverted siphon or
depressed sewer that runs under full gravity flow, at a pressure above the atmospheric pressure, the profile
being depressed below the hydraulic grade line. Inverted siphons are used to pass sewer lines, under
obstacles such as buried pipes, subways and stream beds. The pipe used must be above to withstand
internal pressure. As high velocities as possible should be maintained, with 0.9m/sec minimum.
Inverted siphon may consist of one, two or more pipes depending upon the amount of flow and head
available.
Lamp Holes
Lamp holes consists of a vertical A.C. pipe of 22.5cm diameter and
connected to the main sewer
1. Distance between the man holes is usually large and it is not possible
to approach full length from both the man holes. Lamp holes are
provided between the man holes.
2. They may be used under certain circumstances for flushing the sewer
line.
3. By providing a perforated cover, the ventilation of the sewer can be
achieved.
Leaping Weir
It consists of a gap in the invert of the
combined sewer. The intercepting sewer
runs at a lower level and at the right angles
to the combined sewer.
When the flow in the combined sewer is
only D.W.F the whole flow directly falls
into the intercepting sewer through the gap.
But as the discharged exceed the
predetermined amount, the excess sewage
jumps or the leap across the gap and is
carried to the natural stream or river
through storm water sewer.
Junction chamber
It is the chamber constructed
to facilitate the junction of
two or more sewers, which
are large enough for a man to
enter.
main sewer
unit-I.pptx
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unit-I.pptx

  • 1. ENVIRONMENTAL ENGINEERING –II Course Learning Objectives: The objective of this course is: • Outline planning and the design of wastewater collection, conveyance and treatment systems for a community/town/city • Provide knowledge of characterisation of wastewater generated in a community • Impart understanding of treatment of sewage and the need for its treatment. • Summarize the appurtenance in sewerage systems and their necessity • Teach planning, and design of septic tank and imhoff tank and the disposal of the effluent from these low cost treatment systems • Effluent disposal method and realise the importance of regulations in the disposal of effluents in rivers Course Outcomes: By the end of successful completion of this course, the students will be able to: • Plan and design the sewerage systems • Select the appropriate appurtenances in the sewerage systems • Analyze sewage and suggest and design suitable treatment system for sewage treatment • Identify the critical point of pollution in a river for a specific amount of pollutant disposal into the river • Suggest a suitable disposal method with respect to effluent standards.
  • 2. SYLLABUS: UNIT – I: Introduction to Sanitation – Systems of sanitation – relative merits & demerits – collection and conveyance of waste water – sewerage – classification of sewerage systems- Estimation of sewage flow and storm water drainage – fluctuations – types of sewers - Hydraulics of sewers and storm drains– design of sewers – appurtenances in sewerage – cleaning and ventilation of sewers UNIT – II: Pumping of wastewater: Pumping stations – location – components– types of pumps and their suitability with regard to wastewaters. House Plumbing: Systems of plumbing-sanitary fittings and other accessories– one pipe and two pipe systems – Design of building drainage UNIT – III: Sewage characteristics – Sampling and analysis of wastewater - Physical, Chemical and Biological Examination-Measurement of BOD and COD - BOD equations Treatment of sewage: Primary treatment-Screens-grit chambers-grease traps– floatation– sedimentation – design of preliminary and primary treatment units. UNIT – IV: Secondary treatment: Aerobic and anaerobic treatment process comparison. Suspended growth process: Activated Sludge Process, principles, designs, and operational problems, modifications of Activated Sludge Processes, Oxidation ponds, Aerated Lagoons. Attached Growth Process: Trickling Filters–mechanism of impurities removal- classification– Design- operation and maintenance problems. RBCs, Fluidized bed reactors
  • 3. UNIT V: Miscellaneous Treatment Methods: Nitrification and Denitrification – Removal of Phosphates –UASB–Membrane reactors-Integrated fixed film reactors. Anaerobic Processes: Septic Tanks and Imhoff tanks- working Principles and Design–Reuse and disposal of septic tank effluent, FAB Reactors. UNIT – VI: Bio-solids (Sludge) management: Characteristics-SVI, handling and treatment of sludge- thickening – anaerobic digestion of sludge, Sludge Drying Beds. Centrifuge. Disposal of sewage: Methods of disposal – disposal into water bodies-Oxygen Sag Curve-Disposal into sea, disposal on land- sewage sickness. Text Books 1. Wastewater Engineering Treatment and Reuse, Metcalf & Eddy, Tata McGraw-Hill edition. 2. Industrial Water and Wastewater Management, K.V.S.G. Murali Krishna. 3. Elements of Environmental Engineering, K. N. Duggal, S. Chand & Company Ltd. New Delhi, 2012.
  • 4. Introduction to Sanitation UNIT – I Garbage: It is a dry refuse which includes, waste papers, sweepings from streets and markets, vegetable peelings etc. The quantity of garbage per head per day amounts to be about .14 to .24 kg for Indian conditions. Garbage contains large amount of organic and putrefying matter and therefore should be removed as quickly as possible.
  • 5. Refuse: This is the most general term to indicate the wastes which include all the rejects left as worthless, sewage, sullage – all these terms are included in this term. Rubbish: It consists of sundry solid wastes from the residencies, offices and other buildings. Broken furniture, paper, rags etc., Are included in this term. It is generally dry and combustible. Sullage: It is the discharge from the bath rooms, kitchens, wash basins etc., It does not include discharge from the lavatories , hospitals , operation theaters , slaughter houses which has a high organic matter . Sewage : It is a dilute mixture of the wastes of various types from the residential, public and industrial places . It includes sullage water and foul discharge from the water closets, urinals, hospitals, stables ,etc.
  • 6. Invert: It is the lowest point of the interior of the sewer at any c/s. Sludge: It is the organic matter deposited in the sedimentation tank during treatment. Storm water : It is the surface runoff obtained during and after the rainfall which enters sewers through inlet. Storm water is not foul as sewage and hence it can be carried in the open drains and can be disposed off in the natural rivers without any difficulty. Sanitary sewage : It is the sewage obtained from the residential buildings & industrial effluents establishments‘. Being extremely foul it should be carried through underground conduits. Bacteria: These are the microscopic organisms. The following are the groups of bacteria: Aerobic bacteria: they require oxygen &light for their survival. Anaerobic bacteria: they do not require free oxygen and light for survival. Facultative bacteria: they can exist in the presence or absence of oxygen. They grow more in absence of air.
  • 7. Domestic sewage: It is the sewage obtained from the lavatory basins, urinals &water closets of houses, offices & institutions. It is highly foul on account of night soil and urine contained in it. Night soil starts putrefying & gives offensive smell. It may contain large amount of bacteria due to the excremental wastes of patients. This sewage requires great handling &disposal. Industrial sewage: It consists of spent water from industries and commercial areas. The degree of foulness depends on the nature of the industry concerned and processes involved. Sewers: Ewers are underground pipes which carry the sewage to a point of disposal. Sewerage: The entire system of collecting, carrying &disposal of sewage through sewers is known as sewerage. Dry weather flow (DWF): Domestic sewage and industrial sewage collectively, is called as DWF. It does not contain storm water. It indicates the normal flow during dry season.
  • 8. Different Methods of domestic waste water disposal include (Systems of Sanitation) 1. Conservancy system 2. Water carriage system Conservancy system Sometimes the system is also called as dry system. This is out of date system but is prevailing in small towns and villages. Various types of refuse and storm water are collected conveyed and disposed of separately. Garbage is collected in dustbins placed along the roads from where it is conveyed by trucks ones or twice a day to the point of disposal. all the non combustible portion of garbage such as sand dust clay etc., are used for filling the low level areas to reclaim land for the future development of the town. The combustible portion of the garbage is burnt. The decaying matters are dried and disposed of by burning or the manufacture of manure. Water carriage system With development and advancement of the cities urgent need was felt to replace conservancy system with some more improved type of system in which human agency should not be used for the collection and conveyance of sewage .After large number of experiments it was found that the water is the only cheapest substance which can be easily used for the collection and conveyance of sewage. As in this system water is the main substance therefore it is called as water carriage system.
  • 9.
  • 10. Relative Merits & Demerits of Sanitation Merits • the fundamental principles of sanitation of the community is to remove all decomposable matter, solid waste, liquid or gaseous away from the premises of dwellings as fast as possible after it is produced, to a safe place , without causing any nuisance and dispose it in a suitable manner so as to make it permanently harmless. Demerits • If proper arrangements for the collection, treatment and disposal are not made, they will go on accumulating and create foul condition. • If untreated water is accumulating, the decomposition of the organic materials it contains can lead to the production of large quantity of mal odorous gases. • It also contains nutrients, which can stimulate the growth of aquatic plants and it may contain toxic compounds.
  • 11. Classification of Sewerage Systems 1. Separate system of sewage 2. Combined system of sewage 3. Partially combined or partially separate system Separate system of sewerage In this system two sets of sewers are laid .The sanitary sewage is carried through sanitary sewers while the storm sewage is carried through storm sewers. The sewage is carried to the treatment plant and storm water is disposed of to the river. Combined system of sewage When only one set of sewers are used to carry both sanitary sewage and surface water. This system is called combined system. Sewage and storm water both are carried to the treatment plant through combined sewers Partially combined or partially separate system A portion of storm water during rain is allowed to enter sanitary sewer to treatment plants while the remaining storm water is carried through open drains to the point of disposal.
  • 12. Estimation of sewage flow Sanitary sewage is mostly the spent water of the community into sewer system with some groundwater and a fraction of the storm runoff from the area, draining into it. Before designing the sewerage system, it is essential to know the quantity of sewage that will flow through the sewer. The sewage may be classified under two heads: 1. The sanitary sewage, and 2. Storm water Sanitary sewage is also called as the Dry Weather Flow (D.W.F), which includes the domestic sewage obtained from residential and residential and industrials etc., and the industrial sewage or trade waste coming from manufacturing units and other concerns. Storm water consists of runoff available from roots, yards and open spaces during rainfall. Quantity of Sewage It is usual to assume that the rate of sewage flow, including a moderate allowance for infiltration equals to average rate of water consumption which is 135 litre/ head /day according to Indian Standards. It varies widely depending on size of the town etc. this quantity is known as Dry Weather Flow (D.W.F). It is the quantity of water that flows through sewer in dry weather when no storm water is in the sewer. Rate of flow varies throughout 24 hours and is usually the greatest in the fore-noon and very small from midnight to early morning. For determining the size of sewer, the maximum flow should be taken as 3 * D.W.F.
  • 13. Design Discharge of Sanitary Sewage The total quantity of sewage generated per day is estimated as product of forecasted population at the end of design period considering per capita sewage generation and appropriate peak factor. The per capita sewage generation can be considered as 75 to 80% of the per capita water supplied per day. Factors affecting the quantity of sewage flow 1. Population 2. Type of area 3. Rate of water supply 4. Infiltration and exfiltration Design Period The future period for which the provision is made in designing the capacities of the various components of the sewerage scheme is known as the design period. The design period depends upon the following: 1. Ease and difficulty in expansion 2. Amount and availability of investment 3. Anticipated rate of population growth, including shifts in communities, industries and commercial investments 4. Hydraulic constraints of the systems designed 5. Life of the material and equipment
  • 14. Fluctuations in sewage flow The sewage flow, like the water supply flow, is not constant in practice but varies. The fluctuation may, in a similar way, be seasonal or monthly, daily and hourly. Variation occurs in the flow of sewage over annual average daily flow. Fluctuation in flow occurs from hour to hour and from season to season. The typical hourly variation in the sewage flow is shown in the Figure. The first peak flow generally occurs in the late morning it is usually about 200 percent of the average flow while the second peak flow generally occurs in the early evening between 6 and 9p.m. and the minimum flow occurring during the night after twelve or early hours of the morning is generally about half of the average flow. Due to variation in discharge, the depth of flow varies, and hence the hydraulic mean depth (r) varies. Due to the change in the hydraulic mean depth, the flow velocity (which depends directly on r2/3) gets affected from time to time. It is necessary to check the sewer for maintaining a minimum velocity of about 0.45 m/s at the time of minimum flow (assumed to be 1/3rd of average flow). The designer should also ensure that a velocity of 0.9 m/s is developed at least at the time of maximum flow and preferably during the average flow periods also. Moreover, care should be taken to see that at the time of maximum flow, the velocity generated does not exceed the scouring value.
  • 15. Quantity of storm water flow When rain falls over the ground surface, a part of it percolates into the ground, a part is evaporated in the atmosphere and the remaining part overflows as storm water. This quantity of storm water is very large as compared with sanitary sewage. Factors affecting storm water The following are factors which affect the quantity of storm water: 1. Rainfall intensity and duration. 2. Area of the catchment. 3. Slope and shape of the catchment area. 4. Nature of the soil and the degree of porosity. 5. Initial state of the catchment.
  • 16. Estimate of quantity of storm water Generally there are two methods by which the quantity of storm water is calculated: 1. Rational method 2. Empirical formulae method Rational method Runoff from an area can be determined by the Rational Method. The method gives a reasonable estimate up to a maximum area of 50 ha (0.5 Km2). Where, Q= quantity of storm water in m3/sec C= coefficient of runoff i= intensity of rainfall A= area of drainage in hectare the value of runoff coefficient, C is varies from 0.01 for forest or wooded area to 0.95 for a water tight roof surfaces. Runoff coefficient (overall) C = Where: A1, A2 ,A3….are different types of area and C1, C2, C3…..are their runoff coefficient respectively.
  • 17. Empirical formula method For determining the runoff from very large areas, generally empirical formulae are used. All the empirical formulae are applicable only under certain specific conditions such as slope of land, imperviousness, rate of rainfall etc.
  • 18. Time of concentration The time taken for the maximum runoff rate to develop, is known as the time of concentration, and is equal to the time required for a drop of water to run from the farthest point of the watershed to the point for which the runoff is to be calculated. The time of concentration refers to the time at which the whole area just contributes runoff to a point. Tc= te+tf Where, tc = time of concentration te = time of entry to the inlet (usually taken as 5 – 10 min) tf = time of flow in the sewer Time of concentration is made up of inlet time (over land flow) and channel flow time. Time of entry (inlet time or overland flow): is the time required for water to reach a defined channel such as a street gutter, plus the gutter flow time to the inlet. Channel flow time: is the time of flow through the sewers to the point at which rate of flow is being assessed. For application of the rational method, TxDOT recommends that tc be less than 300 minutes (5 hours) and greater than 10 minutes. Morgali and Linsley Method For small urban areas with drainage areas less than ten or twenty acres, and for which the drainage is basically planar, the method developed by Morgali and Linsley (1965) is useful. It is expressed as where: tc = time of concentration (min), i = design rainfall intensity (in/hr), n = Manning surface roughness (dimensionless), L = length of flow (ft), and S = slope of flow (dimensionless).
  • 19. Kirpich Method For small drainage basins that are dominated by channel flow, the Kirpich (1940) equation can be used. The Kirpich equation is tc = 0.0078(L3/h)0.385 where: tc = time of concentration (min), L = length of main channel (ft) h = relief along main channel (ft). The Kirpich method is limited to watershed with a drainage area of about 200 acres. Kerby-Hatheway Method For small watersheds where overland flow is an important component, but the assumptions inherent in the Morgali and Linsley approach are not appropriate, then the Kerby (1959) method can be used. The Kerby- Hatheway equation is tc = (0.67NL/√S)0.467 where: tc = time of concentration (min), N = Kerby roughness parameter (dimensionless) S = overland flow slope (dimensionless).
  • 20.
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  • 23. Types of sewer according to material 1. Asbestos Cement (AC) Sewer 2. Brick Sewer 3. Cement Sewer 4. Cast iron (CT) Sewer 5. Steel Sewers 6. Plastic Sewers Types of sewer according to shapes Sewers are generally circular pipes laid below ground level, slopping continuously towards the outfall. These are designed to flow under gravity. Mostly sewers of circular shape are used in all the sewerage schemes, because of the following facts: • It affords least perimeter and hence construction material required is minimum. • They are easy to construct and handle. • Since it has no corners, there are less chances of deposition of organic matters. • They possess excellent hydraulic properties. However, sewers of non circular shapes are used for the following reasons. • To develop self cleansing velocity in the sewer, when the flow is minimum. • To effect economy in the construction. • To increase the headway so that a man can enter easily for repairs, and cleaning.
  • 24. Following are the non-circular shapes of sewers which are commonly used for sewers: New/ Modified Egg shaped Sewer Box or rectangular sewers Basket-Handle Section Horse shoe sewer section U-shaped section Semi-circular Section Semi-elliptical section Parabolic section
  • 25. Self cleansing velocity It is necessary to maintain a minimum velocity in a sewer line to ensure that suspended solids do not deposit and cause choking troubles. Such a minimum velocity is called as self cleansing velocity. Self cleansing velocity is determined by considering the particle size and specific weight of the suspended solids in sewage. The velocity which can cause automatic self cleansing can be found out by the following formula given by Shield: V = √ [(8K/f) ((SS-S)/S) g d] Where: f = Darcy‘s co-efficient of friction,0.03 K = characteristics of solid particles = 0.06 for organic and = 0.04 for inorganic solids SS = specific gravity of particles = 2.65 for inorganic and = 1.2 for organic solids S = specific gravity of sewage, 1.0 G = acceleration due to gravity D = diameter of particle Hydraulics of sewers and storm drains Dia. of sewers in mm Self cleansing velocity in m/sec 150-300 1.0 300-600 0.75 >600 0.6 As per Badmin Lathom's recommendations
  • 26. Empirical formulae used in design of sewers Chezy‘s formula: V = C √R.S (or) C √mi Where, V = velocity of flow in m/sec R = hydraulic mean depth in m S = slope of the sewer = Fall of sewer/length C = Chezy‘s contact. Kutter‘s formula for Chezy‘s contact is given by: C = [23 + (0.00155/S) + (1/n)] [ 1 + (23 + (0.00155/S))(n/√R) ] Where, n = coefficient of roughness or rughosity factor Manning‘s formula: V = (1/n) R2/3 S1/2 Crimp‘s and Burge‘s formula: V = 83.33 R2/3 S1/2 Hazen –Williams formula: V = 0.85 C R0.6 S0.54 the value of C varies depending upon the surfaces. S no. Material of sewer Value of n 1. Brick sewers a) Flush pointed 0.015 b) Plastered smooth 0.013 2. Stoneware sewers 0.014 3. Cast iron 0.013 4. Smooth earthen channel 0.020 5. Rough channel 0.030 S no. Type of material Value of C 1 Stoneware pipes in good condition 110 2 New cast iron 130 3 Very smooth surfaces 140
  • 27. Hydraulic Characteristics of Circular Sewer Running Full or Partially Full Hydraulic Mean Depth, R(or)m = A/P Solving for half full sewer, R(or)m = D/4 Non-scouring velocity The permissible maximum velocity to prevent eroding is termed as non- scouring velocity and it should be limited to 3.0 m/s. Design of sewers
  • 28.
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  • 32.
  • 33.
  • 34. Testing of sewer line It is necessary to test the sewer after its laying for water tightness before backfilling of the excavted earth. Smoke test: This test is performed for soil pipes, vent pipes laid above ground. The test is conducted under a pressure of 2.5m of water and maintained for 15 minutes after all trap real have been filled with water. The smoke is produced by burning oil waste or tar paper in combustion chamber of a smoke machine. Water test: This test is performed for underground sewer pipes before back filling is done. The test should be carried out by suitably plugging the lower end of the drain and filling the system with water. A knuckle band shall be temporarily jointed at the top end and a sufficient length of vertical pipe is jointed so as to provide the required test head. Subsidence of test water may be due to Absorption by pipes and joints Leakages at joints etc. Any leakage if visible and defective part of work if any should be made good. Test for straightness and obstruction: For this test, a mirror is placed in front of one end of sewer and the image of the section is observed. If the sewer line is straight, the image should be circular. If it is not a complete circle, then it is not straight. For testing for obstruction, by inserting a steel call at upper end and if there is no obstruction in the sewer line, the call will emerge out from the lower end.
  • 35. Sewer Appurtenances Proper functioning and to facilitate maintenance of the sewage system, various additional structures have to be constructed on the sewer lines. These structures are known as sewer appurtenances. Following are the important appurtenances. 1.Manholes 2.Inlets 3.Catch basins Manholes The manholes are R.C.C or masonry chambers constructed on the sewer line to facilitate a man to enter the sewer line and make the necessary inspection and repairs. These are fitted with suitable cast iron covers. The manholes should be installed at every points where there is a change in direction, change in pipe size, or considerable change in gradient. 4.Flushing devices 5.Regulators 6.Inverted siphons 7.Grease and oil traps 8.Lamp holes 9.Leaping weirs 10.Junction chambers
  • 36. Inlets These are meant to admit the surface runoff to the sewers and form a very important part of the system. Their location and design should therefore be given careful consideration. Catch Basins Catch basins are the structures of pucker chamber and a stout cover. They are meant for the retention of suspended grit, sludge and other heavy debris and floating rubbish from rain water which otherwise might have entered and cause choking problems.
  • 37. Flushing devices Flushing tanks are provided to flush the sewers. They are seldom used. At such places where self cleansing velocity is not developed or when the ground is flat and it is not possible to lay the sewer lines at designed gradients, flushing tanks required to flush the sewer line. Grease and Oil traps The sewage from kitchens of hotels and restaurants and industries contains oil and grease and fats. If these oils and greases are not removed from the sewage they will stick to the interior surface of the sewer and clogging.
  • 38. Regulators A Regulator is a device that diverts sewage flow from one sewer into another. The regulator usually goes into action when the sewage flow reaches a predetermined amount. It may then divert all the sewage or only that part above the predetermined flow at which it begins to function. Regulators are mostly used where combined sewers discharge into interceptors. Inverted siphons The true siphon is a sewer that runs full having its flow line above the hydraulic grade line. The pressure in the sewer line will be greater than atmospheric pressure. On the other hand inverted siphon or depressed sewer that runs under full gravity flow, at a pressure above the atmospheric pressure, the profile being depressed below the hydraulic grade line. Inverted siphons are used to pass sewer lines, under obstacles such as buried pipes, subways and stream beds. The pipe used must be above to withstand internal pressure. As high velocities as possible should be maintained, with 0.9m/sec minimum. Inverted siphon may consist of one, two or more pipes depending upon the amount of flow and head available.
  • 39.
  • 40. Lamp Holes Lamp holes consists of a vertical A.C. pipe of 22.5cm diameter and connected to the main sewer 1. Distance between the man holes is usually large and it is not possible to approach full length from both the man holes. Lamp holes are provided between the man holes. 2. They may be used under certain circumstances for flushing the sewer line. 3. By providing a perforated cover, the ventilation of the sewer can be achieved. Leaping Weir It consists of a gap in the invert of the combined sewer. The intercepting sewer runs at a lower level and at the right angles to the combined sewer. When the flow in the combined sewer is only D.W.F the whole flow directly falls into the intercepting sewer through the gap. But as the discharged exceed the predetermined amount, the excess sewage jumps or the leap across the gap and is carried to the natural stream or river through storm water sewer.
  • 41. Junction chamber It is the chamber constructed to facilitate the junction of two or more sewers, which are large enough for a man to enter. main sewer