SlideShare a Scribd company logo
1 of 85
Download to read offline
1
TYPES OF SEDIMENTATION TANKS
1. Quiescent or fill and draw type:
 Rectangular in plan.
 Water is filled, allowed for retention period of 30 to 60 hrs (normally
24 hrs) then clear water is drawn from outlet
 Empty the tank and cleaning of sediment is done.
 Needs more detention period, labours and supervision,
 More than one tanks
 Not used nowadays.
2
2. Continuous type:
A. Horizontal Flow Type
(a) Rectangular tanks with longitudinal flow
3
(b) Circular with radial flow
i. Circular with central feed ii. Circular with peripheral feed
4
B. Vertical Flow Type
5
Surface loading or surface overflow rate (SOR) of sedimentation
tank:
6
PROCESS OF SEDIMENTATION WITH COAGULATION
1. Feeding the coagulant
Dry feeding
Wet Fedding
2. Mixing of coagulant
a. Mixing basin with baffle walls
b. Mixing basin with mechanical means
c. Mixing channels
d. Hydraulic jump method
e. Compressed air method
f. Centrifugal pumping method
3. Flocculation
4. Sedimentation
7
a. Mixing basin with baffle walls
i. Horizontal or round end type:
8
ii. Vertical or over and under type
9
b. Mixing basin with mechanical means
10
3. Flocculation
11
12
4. Sedimentation
13
FILTER AND THEIR CLASSIFICATION
1. Slow sand filter (SSF)
14
a. Enclosure tank:
 depth = 2.5 – 3.5 m
 surface area = 10 – 2000 m2
 filtration rate = 100 – 200 lph/m2
 cross slope = 1 in 100 – 1 in 200 towards central drain
b. Filter media:
• sand layer = 90 – 110 cm thick
• effective size (D10) = 0.25 – 0.35 mm (0.3 mm is common)
• coefficient of uniformity (Cu) = 3 – 5.
c. Base material:
• 30 to 75 cm thick gravel
• four layers of each about 15 cm
• 3 – 6 mm, 6 – 20 mm, 20 – 40 mm and 40 – 65 mm from the
top
e. Appurtenances: vertical air pipes, depth controlling
devices,head loss measuring device, rate maintaining devices
etc
15
d. Under drainage system:
Efficiency of SSF:
 98 – 99% bacteria removal
 removes turbidity up to 50 ppm
 Only 20 – 25 % of color removal
 not so efficient in removal of colloidal matters
16
2. Rapid sand filter (RSF)
17
a. Enclosure tank:
 depth = 2.5 – 3.5 m
 surface area = 10 – 50 m2
 filtration rate = 3000 – 6000 lph/m2
 Length width ratio = 1.25 – 1.35
b. Filter media:
 sand layer = 60- 90 cm thick
 effective size (D10) = 0.35 – 0.60 mm
 coefficient of uniformity (Cu) = 1.3-1.7.
c. Base material:
• 45 to 60 cm thick gravel
• four layers of each about 15 cm
• 2 – 6 mm, 6 – 12 mm, 12 – 20 mm and 20 – 50 mm from the
top
18
d. Under drainage system:
19
e. Appurtenances:
Wash water trough, air
compressor, rate
control device, head
loss indicators meters,
valves etc
Efficiency of RSF:
 35-40 ppm turbidity removal
 removes colour below 3 ppm
 Less efficient in iron and manganese removal
 not efficient in odour removal
 Less efficient in bacteria removal (Only 80 – 90 %)
20
3. Pressure filter (PF)
water is passed under pressure of 3 – 7 kg/cm2 through pumping
 Rate of filtration of PF is 6000 – 15000 lit/hr/m2 of filter area
 low efficient than RSF for the removal of color, turbidity and bacterial
load
 can be used for small colonies, industry and swimming pools etc.
Difference between
21
Criteria Slow sand filter Rapid sand filter
Filtration rate LPH/M2 100 – 200 3000-6000
Filter Media :sand layer (cm) 90 – 110 60-90
effective size (D10) mm 0.25 – 0.35 0.35-0.6
coefficient of uniformity (Cu) 3 – 5. 1.3-1.7
Efficiency bacteria removal 98 – 99% Less efficient (Only
80 – 90 %)
22
DISINFECTION
 To kill pathogens
 Chemicals called disinfectants
Characteristics of a good disinfectants:
1.Should be able to destroy all harmful bacteria
economically within the contact time and in the wide
range of temperature and pH values.
2.It should not render the water toxic or impart colour and
odour.
3.It should be easily available at reasonable cost.
4.It should be safe to handle and method of application
should be simple.
5.It should persist in residual concentrations as safeguard
recontamination.
23
Methods of disinfection: Chlorination
• When Chlorine is used Cl2 + H2O ↔ HOCl + H+ + Cl –
[Called Hydrolysis reaction occurs at 49 - 212°C]
The HOCl further dissociates (ionizes) as follows
HOCl ↔ H+ + OCl – [Called Ionization reaction]
HOCl and OCl – penetrate cell walls and reacts with the enzyme
system in the cell of micro-organism and results death of micro-
organism
24
FORMS OF APPLICATION OF CHLORINE
(a) Bleaching powder
CaOCl2 ↔ Ca++ + 2 OCl –
H+ + OCl – ↔ HOCl –
this process is called hypochlorination
(b) Chloramines
H2O + Cl2↔ HOCl + H++ Cl –
NH3 + HOCl ↔ NH2Cl (monochloramine) + H2O
NH2Cl + HOCl ↔ NHCl2 (dichloramine) + H2O
NHCl2 + HOCl ↔ NCl3 (trichloramine) + H2O
(c) Chlorine gas or liquid chlorine
(d) Chlorinedioxide
2NaClO2 + Cl2 ↔ 2NaCl + 2 ClO2↑
25
CHLORINE DEMAND AND DOSE
(a) Chlorine demand
Chlorine demand = Total amount of chlorine added – Amount of
residual chlorine required after a specified contact period
Reaction for combined available chlorine:
Cl2 + H2O ↔ HOCl + H++ Cl –
NH3 + HOCl ↔ NH2Cl (monochloramine) + H2O
NH2Cl + HOCl ↔ NHCl2 (dichloramine) + H2O
NHCl2 + HOCl ↔ NCl3 (trichloramine) + H2O
(b) Chlorine dose
Quantity of chlorine required to be added to water to leave 0.2 mg/l
or ppm of freely available residual chlorine after 10 minutes of
contact period
26
FORMS OF CHLORINATION
1. Plain chlorination or simple chlorination:
To raw water
2. Pre-chlorination:
Before treatment
3. Post chlorination:
After treatment
4. Double or multiple chlorination:
Two or more point
5. Super chlorination:
Application beyond break point
6. De-chlorination
Removing chlorine
7. Break point chlorination or free residual chlorination:
27
7. Break point chlorination or free residual chlorination:
28
FACTORS AFFECTING BACTERIAL EFFICIENCY OF
CHLORINE
1.Turbidity: low efficient
2.Presence of metallic compound: Efficiency is
decreased.
3.Ammonia compound: Efficiency is decreased
4.pH value of water: If pH is high in water, efficiency is
low
5. Temperature: If temperature decreased, efficiency
decreased.
6.Time of contact: time of contact should be at least 30
minutes.
7.Type, condition and concentration of micro-organism:
Efficiency low if the favorable condition for bacteria is
available and concentration of bacteria is high.
29
WATER SOFTENING
• Process of removing hardness
• Purpose: To remove Hardness
A. Removal of temporary hardness:
(a) Boiling:
It is costlier and not used in public water supply.
Ca(HCO3)2 CaCO3↓ + CO2↑ + H2O
Mg(HCO3)2 MgCO3↓ + CO2 ↑+ H2O
(b) Adding lime:
Ca(HCO3)2 + Ca(OH)2 → 2CaCO3↓ + 2H2O
Mg(HCO3)2 + Ca(OH)2 → CaCO3↓ + MgCO3↓ + 2H2O
30
A. Removal of permanent hardness:
a. Lime soda process:
CO2 + Ca(OH)2 = CaCO3↓ + H2O
Ca(HCO3)2 + Ca(OH)2 = 2CaCO3↓ + 2H2O
Mg(HCO3)2 + Ca(OH)2 = CaCO3↓ + MgCO3 + 2H2O
MgCO3 + Ca(OH)2 = Mg(OH)2↓ + CaCO3↓
MgSO4 + Ca(OH)2 = Mg(OH)2↓ + CaSO4
CaSO4 + Na2CO3 = CaCO3↓ + Na2SO4
MgCl2 + Ca(OH)2 = Mg(OH)2↓ + CaCl2
CaCl2 + Na2CO3 = CaCO3↓ + 2NaCl
MgCl2 + Na2CO3 = MgCO3 + 2NaCl










+





→










+
2NaCl
SONa
2NaHCO
Z
Mg
Ca
Cl
SO
)(HCO
Mg
Ca
ZNa 42
3
2
4
23
2
b. Permutit Process:
31
b. Permutit Process:
32
C. Demineralization or deionization process:
Regeneration of zeolite:
22 Cl
Mg
Ca
ZNa2NaClZ
Mg
Ca






+→+














 +
+





→










+
2HCl
SOH
2COO2H
R
Mg
Ca
Cl
SO
)(HCO
Mg
Ca
RH 42
22
2
4
23
2
Regeneration of hydrogen exchanger:
















+→+










2
4
2
42
2
Cl/Cl
SO
2Na
Mg
Ca
RH
HCl
SOH
R
Na
Mg
Ca
33
MISCELLANEOUS TREATMENT
A. Aeration:
(A) Aeration
(B) Removal of iron and manganese
(C) Removal of colour odour and taste
Purpose of aeration:
1. To make water fresh by absorbing oxygen from air.
2. To release dissolved gases (CO2, H2S etc) to
atmosphere.
3. To remove bad taste and odour.
4. To reduce corrosiveness of water.
5. To precipitate Fe and Mn to some extent by oxidizing.
6. To kill harmful bacteria to some extent.
7. To mix mixing chemicals to water.
34
35
Methods of aeration:
Free fall or gravity aerators:
36
37
Methods of aeration:
Free fall or gravity aerators:
Mechanical aerators:
38
Free fall or gravity aerators:
39
40
41
B. Removal of iron and manganese:
Effect:
i. Produce taste, odour and brown red colour.
ii.Stains on clothes, corrosion and clogging of pipes by
accumulation of precipates.
iii.Causes difficult in various industrial process.
Purpose: Removal of iron and manganese
Methods:
(a) By aeration
(b) By adding lime
(c) Passing over manganese zeolite
42
(a) By aeration: In this case aeration is done before
sedimentation.
Fe:
4Fe + O2 + 10 H2O → 4Fe(OH)3 ↓ + 8H
Fe(HCO3)2 :
Fe(HCO3)2 + 2H2O → FeO + 2CO2 + 3H2O
4FeO + O2 → 2Fe2O3
Fe2O3 + 3H2O → 2Fe(OH)3 ↓
Mn:
6Mn + 3O2 + 6H2O → 6MnO2 ↓ + 12H
43
C. Removal of colour, odour, taste:
Purpose: Removal of colour, odour and taste
Methods:
(a) By aeration
(b) By activated carbon treatment
• Activated carbon is manufactured by heating saw
dust, paper mill waste etc. at 500°C in a closed vessel
in controlled condition of burning at 800°C.
• readily available in market in powder or granular
form
• absorbs organic matters and removes colour, odour
and taste.
(c) Using copper sulphate: in swimming pools
SODIS method is very easy to
apply: A transparent PET bottle is
cleaned with soap. Then, the bottle
is filled with water and placed in
full sunlight for at least 6 hours.
The water has then been
disinfected and can be drunk.
Membrane Filtration
45
46
Reverse Osmosis
47
48
BIO SAND FILTER
• (BSF) is a point-of-use water treatment system adapted
from traditional slow sand filters.
• Bio sand filters remove pathogens and suspended solids
from water using biological and physical processes that take
place in a sand column covered with a bio film.
• BSFs have been shown to remove heavy metals, turbidity,
bacteria, viruses and protozoa.
• BSFs also reduce discoloration, odor and unpleasant taste.
• Studies have shown a correlation between use of BSFs and
a decrease in occurrence of diarrhea because of their
effectiveness, ease of use, and lack of recurring costs, bio
sand filters are often considered appropriate technology in
developing countries.
How Well Does the Bio sand Filter Work?
• Water naturally contains many living things. Some are harmless and
others can make people sick. Living things that cause disease are also
known as pathogens. They are sometimes called other names, such
as microorganisms, microbes or bugs, depending on the local
language and country.
• There are four different categories of pathogens that are : bacteria,
viruses, protozoa and helminths.
• Turbid water looks cloudy, dirty or muddy and is caused by sand, silt
and clay that are floating in the water. Drinking turbid water will not
make people sick by itself.
• However, viruses, parasites and some bacteria can sometimes attach
themselves to the suspended solids in water.
• This means that turbid water usually has more pathogens so drinking
it increases the chances of becoming sick
56
CHAPTER 7: INTRODUCTION TO CONVEYANCE
• Transportation of water to treatment plant or reservoir or
distribution through conduits.
• Transmission: Source – TP – Reservoir
• Distribution: Reservoir – Users Tap
• Conduits:
A. Gravity: Open channel flow
Canals, aqueducts, tunnels
B. Pressure
Pipes, pressure tunnels, pressure aqueducts etc.
57
PIPE, PIPE MATERIALS AND PIPE TYPES
Pipe:
• Circular conduit where fluid flows under pressure
• Designed to carry external and internal loads
Requirement of good pipe:
• Withstand external, internal and temperature stresses
• Smooth for minimum frictional losses
• Durable
• Light
• Noncorrosive
• Cheap
• Easy joint
58
Pipe types as per materials:
59
(a) Cast Iron (CI) Pipe:
• Manufactured by sand molding or centrifugal method
• Standard 1.8 m length but up to 3m for smaller diameter
• 50 mm to 1.2 m dia.
Advantages:
Easy to join, can withstand high pressure, resistance to
corrosion, long life (> 100 yrs), durable, strong and moderate
in cost, joined by flanged or Spigot and socket joint, low
maintenance cost.
Disadvantages:
Brittle and very heavy so difficult to transport and may be
expensive.
Suitability: Suitable for distribution system.
60
(b) Wrought Iron (WI) Pipe:
• Manufactured by rolling the flat plates of metal to
proper diameter and welding to the edges
Advantages:
Strong, light weight, can withstand high pressure (400
m) and cheaper than CI pipes
Disadvantages:
It can’t withstand external load and when there is no
water inside, liable to corrosion and costly to maintain.
It is costlier than CI pipes
Suitability: Occasionally used for main lines where
pressure is high
61
(c) Steel Pipe:
• Manufactured by WI or mild steel which are galvanized by
providing a protective coating of zinc on inner and outer surface
Advantages:
It is cheap, light, easy in handling and transport, easy in joining with
screwed socket joints and 20 years of life, resistant to corrosion
when exposed to atmosphere
Disadvantages:
may get corroded by acidic and alkaline waters and liable to
incrustation.
Suitability: main lines where pressure is high and when pipe is
exposure in open atmosphere
62
(d) Galvanized iron (GI) pipes:
• Manufactured similar as WI pipes
• 15,20,25,32,40,50,63,75,90,110,125,150, 200 mm inner dia
Advantages:
Light in weight, easy in transport, handling, cutting, threading,
working, joining, and gives neat appearance, joined couplings or
screwed socket joint.
Disadvantages:
Costly, corrosive and less durable than CI pipes
Suitability: Inside plumbing in buildings but not used nowadays due
to high cost.
63
(e) Concrete (GI) pipes:
• Made of cement concrete (precast or cast in site)
Advantages:
Withstand 150 m head of water, resist corrosion and life is above
75 years, maintenance cost is low, least thermal expansion, can be
laid under water and resist normal traffic load
Disadvantages:
Precast type is heavy to handle and transport, concrete pipes can’t
resist high pressure and difficult to repair, it may be affected by
acids and alkali and salty waters, difficult to join and liable to leak
due to porosity
Suitability:
Where water does not flow under pressure (i.e. sewerage system)
64
(f) Asbestos cement (AC) pipes:
• Made of mixture of cement and asbestos fibers
Advantages:
not affected by salt water and corrosive materials, smooth,
light so easy in handling
Disadvantages:
Affected by alkali and acid and also brittle so costlier in
transport.
Suitability:
Small size distribution pipes
65
(g) Wooden pipes:
• made of wood by making channels or boring at center and used
in ancient times
• not used in water supply nowadays
(h) Vitrified clay Pipes:
• made of vitrified clay so has smooth surface
• not used in water supply nowadays
(i) Lead and copper Pipes:
• Copper pipe is made of copper and can resist corrosion even if
water contains some acids and expensive so not used in water
supply nowadays
• Leads are soluble in water so lead pipe causes lead poisoning
hence it is not used in water supply nowadays.
66
(f) Plastic Pipes:
• Made of Plastic and common in nowadays
• it is corrosion resistant, light in weight and economical
Advantages:
Light, cheap, available in longer length, electrical insulation,
corrosion free, life correspond to GI
Disadvantages:
Less resistant to hot water, may impart smell to water, can be easily
cut.
Suitability:
All water sypply systems
67
Types:
1. Low density polyethylene (LDPE) pipes:
Used in electrical wiring
2. High density polyethylene (HDPE)pipes
3. Polyvinyl chloride (PVC) pipes:
4. Unplastisized Polyvinyl chloride (UPVC) pipes:
5. Poly Propylene Random (PPR) Pipes:
Plastic Pipes
68
LAYING OF PIPES
1.Preparation of detailed maps:
2.Locating proposed alignment of pipeline on the
ground:
3.Location of pipes with respect to ground surface
during laying
4.Excavation of trench:
5.Dewatering of trench:
6.Lowering the Pipes:
7.Joining pipes:
8.Testing of pipes:
9.Back filling and disinfection before first use:
69
70
PIPE JOINTS
71
72
73
74
75
CHAPTER 8: VALVES AND FITTINGS
(a) Sluice or gate or cutoff valve
(b) Reflux or check or non-return valve
(c) Safety or pressure relief valve
(d) Air valve or air relief valve
(e) Drain or scour or blow off valve : Ordinary sluice valve to
remove silt deposit
(f) Butterfly valve and globe valve
Devices used to control the flow of water, regulate pressures,
release air, prevent back flow etc
76
77
78
79
FIRE HYDRANT:
 Devices used for tapping water from mains for the
fire extinguishing, street washing, watering gardens,
flushing sewer lines etc.
 Provided at all road junctions & every 100 – 300 m
apart.
 For tapping water, the hose is connected to the
hydrant and if necessary the engine is used to
increase head.
 It should be cheap, easily connectable & detachable
to the hose pipe and able to give sufficient water. It
may be of post type or flush type.
80
81
FITTINGS
82
83
84
CHAPTER 9: PLANNING OF GRAVITY WATER SUPPLY
• Need identification of scheme
• After need identification, mass meeting is called, prioritize is
done and then scheme acquisition form is filled up and submitted
to VDC, DDC and divisional district water supply office
• With feasibility study report the schemes are forwarded from
divisional office thru regional office to department of water
supply and sewerage (DWSS)
• After obtaining scheme acquisition form list from all 75 districts
, budget ceiling is prepared for forthcoming fiscal year by DWSS
and forward to ministry of concern.
• The ministry approves ceiling consulting with National planning
commission then distributed to DWSS and district offices for
implementation
85
• After obtaining approved budget ceiling, detailed survey
is carried out.
• Detail survey
 horizontal and vertical control and
 questionnaire
• Analysis based on detail survey, the design, drawing,
estimating and costing is done and final report is
prepared.
• Water Users Committee (WUS) is formed and trained in
agreement with WUC or implementation agency
• After agreement, construction is carried out and it is
handover to the WUC.
• WUC are responsible for regular maintenance.

More Related Content

What's hot

Removal of iron &; Manganese
Removal of iron &; ManganeseRemoval of iron &; Manganese
Removal of iron &; ManganeseGAURAV. H .TANDON
 
Ppt coagulation and flocculation
Ppt coagulation and flocculationPpt coagulation and flocculation
Ppt coagulation and flocculationLokesh Saini
 
Plain sedimentation tanks ,Types & Design considerations
Plain sedimentation tanks ,Types & Design considerations Plain sedimentation tanks ,Types & Design considerations
Plain sedimentation tanks ,Types & Design considerations Anshika Saxena
 
3. grit chamber
3. grit chamber3. grit chamber
3. grit chambervvsasane
 
Laying, jointing and testing of pipes
Laying, jointing and testing of pipesLaying, jointing and testing of pipes
Laying, jointing and testing of pipessathyan s
 
Sedimentation Tanks: Design and Working
Sedimentation Tanks: Design and WorkingSedimentation Tanks: Design and Working
Sedimentation Tanks: Design and WorkingRohit Kumar Tiwari
 
WATER & WASTE WATER ENGINEERING - water treatment process & units
WATER & WASTE WATER ENGINEERING -  water treatment process & unitsWATER & WASTE WATER ENGINEERING -  water treatment process & units
WATER & WASTE WATER ENGINEERING - water treatment process & unitsEddy Ankit Gangani
 
Intake structures
Intake structures Intake structures
Intake structures Sachin PatiL
 
Collection and estimation of sewage
Collection and estimation of sewageCollection and estimation of sewage
Collection and estimation of sewageBibhabasu Mohanty
 
Water Treatment Process (Screening)
Water Treatment Process (Screening)Water Treatment Process (Screening)
Water Treatment Process (Screening)Zairul Zaiky
 
2. screen chamber
 2. screen chamber 2. screen chamber
2. screen chambervvsasane
 
Environmental Engineering -II Unit I
Environmental Engineering -II Unit IEnvironmental Engineering -II Unit I
Environmental Engineering -II Unit IGAURAV. H .TANDON
 
Types of sedimentation tank
Types of sedimentation tankTypes of sedimentation tank
Types of sedimentation tankSagar Vekariya
 

What's hot (20)

Removal of iron &; Manganese
Removal of iron &; ManganeseRemoval of iron &; Manganese
Removal of iron &; Manganese
 
Ppt coagulation and flocculation
Ppt coagulation and flocculationPpt coagulation and flocculation
Ppt coagulation and flocculation
 
Plain sedimentation tanks ,Types & Design considerations
Plain sedimentation tanks ,Types & Design considerations Plain sedimentation tanks ,Types & Design considerations
Plain sedimentation tanks ,Types & Design considerations
 
3. grit chamber
3. grit chamber3. grit chamber
3. grit chamber
 
Laying, jointing and testing of pipes
Laying, jointing and testing of pipesLaying, jointing and testing of pipes
Laying, jointing and testing of pipes
 
Filtration in water treatment
Filtration in water treatmentFiltration in water treatment
Filtration in water treatment
 
Sedimentation Tanks: Design and Working
Sedimentation Tanks: Design and WorkingSedimentation Tanks: Design and Working
Sedimentation Tanks: Design and Working
 
L 10 sedimentation
L 10  sedimentationL 10  sedimentation
L 10 sedimentation
 
Aeration
AerationAeration
Aeration
 
WATER & WASTE WATER ENGINEERING - water treatment process & units
WATER & WASTE WATER ENGINEERING -  water treatment process & unitsWATER & WASTE WATER ENGINEERING -  water treatment process & units
WATER & WASTE WATER ENGINEERING - water treatment process & units
 
Design of sewers
Design of sewersDesign of sewers
Design of sewers
 
Intake structures
Intake structures Intake structures
Intake structures
 
Grit chambers
Grit chambersGrit chambers
Grit chambers
 
Collection and estimation of sewage
Collection and estimation of sewageCollection and estimation of sewage
Collection and estimation of sewage
 
Disinfection Process
Disinfection ProcessDisinfection Process
Disinfection Process
 
Water Treatment Process (Screening)
Water Treatment Process (Screening)Water Treatment Process (Screening)
Water Treatment Process (Screening)
 
2. screen chamber
 2. screen chamber 2. screen chamber
2. screen chamber
 
Environmental Engineering -II Unit I
Environmental Engineering -II Unit IEnvironmental Engineering -II Unit I
Environmental Engineering -II Unit I
 
Types of sedimentation tank
Types of sedimentation tankTypes of sedimentation tank
Types of sedimentation tank
 
L 28 disinfection
L 28 disinfectionL 28 disinfection
L 28 disinfection
 

Viewers also liked

water treatment slides
water treatment slideswater treatment slides
water treatment slidesAnand Keshri
 
SEDIMENTATION
SEDIMENTATIONSEDIMENTATION
SEDIMENTATIONErika Joy
 
Filtration and disinfection of water
Filtration and disinfection of waterFiltration and disinfection of water
Filtration and disinfection of waterVinod Kumar Nehta
 
Bs 4-sedimentation
Bs 4-sedimentationBs 4-sedimentation
Bs 4-sedimentationR.K. JAIN
 
Environmental engineering lec 1
Environmental engineering lec 1Environmental engineering lec 1
Environmental engineering lec 1aksar8911
 
Waste water treatment processes
Waste water treatment processesWaste water treatment processes
Waste water treatment processesAshish Agarwal
 
Adopt a-village- sanitation - Clean India Campaign
Adopt a-village- sanitation - Clean India CampaignAdopt a-village- sanitation - Clean India Campaign
Adopt a-village- sanitation - Clean India CampaignNalantha Educational Trust
 
Point-of-Use Water Filtration for Arsenic- A Sustainable and Simple Solution ...
Point-of-Use Water Filtration for Arsenic- A Sustainable and Simple Solution ...Point-of-Use Water Filtration for Arsenic- A Sustainable and Simple Solution ...
Point-of-Use Water Filtration for Arsenic- A Sustainable and Simple Solution ...Stephen Passman, MPH, EMT-B
 
IWRM Evaluation Result_Malaysia
IWRM Evaluation Result_MalaysiaIWRM Evaluation Result_Malaysia
IWRM Evaluation Result_MalaysiaGWP SOUTHEAST ASIA
 
P&G Purifier of water_Indovation 2015_24 January 2015
P&G Purifier of water_Indovation 2015_24 January 2015P&G Purifier of water_Indovation 2015_24 January 2015
P&G Purifier of water_Indovation 2015_24 January 2015India Water Portal
 
Quy trinh u vo cafe voi men vi sinh rhodophos
Quy trinh u vo cafe voi men vi sinh rhodophosQuy trinh u vo cafe voi men vi sinh rhodophos
Quy trinh u vo cafe voi men vi sinh rhodophosSitto Vietnam Co.,Ltd
 

Viewers also liked (20)

Water Quality Control and Treatment Water Treatment
Water Quality Control and Treatment Water Treatment Water Quality Control and Treatment Water Treatment
Water Quality Control and Treatment Water Treatment
 
water treatment slides
water treatment slideswater treatment slides
water treatment slides
 
SEDIMENTATION
SEDIMENTATIONSEDIMENTATION
SEDIMENTATION
 
High Shear Mixers
High Shear MixersHigh Shear Mixers
High Shear Mixers
 
Filtration and disinfection of water
Filtration and disinfection of waterFiltration and disinfection of water
Filtration and disinfection of water
 
Bs 4-sedimentation
Bs 4-sedimentationBs 4-sedimentation
Bs 4-sedimentation
 
Environmental Engineering
Environmental EngineeringEnvironmental Engineering
Environmental Engineering
 
Archit x1 building services 1
Archit x1 building services 1Archit x1 building services 1
Archit x1 building services 1
 
Environmental Engineering-I
Environmental Engineering-IEnvironmental Engineering-I
Environmental Engineering-I
 
Environmental engineering lec 1
Environmental engineering lec 1Environmental engineering lec 1
Environmental engineering lec 1
 
Waste water treatment processes
Waste water treatment processesWaste water treatment processes
Waste water treatment processes
 
Adopt a-village- sanitation - Clean India Campaign
Adopt a-village- sanitation - Clean India CampaignAdopt a-village- sanitation - Clean India Campaign
Adopt a-village- sanitation - Clean India Campaign
 
Point-of-Use Water Filtration for Arsenic- A Sustainable and Simple Solution ...
Point-of-Use Water Filtration for Arsenic- A Sustainable and Simple Solution ...Point-of-Use Water Filtration for Arsenic- A Sustainable and Simple Solution ...
Point-of-Use Water Filtration for Arsenic- A Sustainable and Simple Solution ...
 
Disinfection
DisinfectionDisinfection
Disinfection
 
IWRM Evaluation Result_Malaysia
IWRM Evaluation Result_MalaysiaIWRM Evaluation Result_Malaysia
IWRM Evaluation Result_Malaysia
 
Filtration
FiltrationFiltration
Filtration
 
P&G Purifier of water_Indovation 2015_24 January 2015
P&G Purifier of water_Indovation 2015_24 January 2015P&G Purifier of water_Indovation 2015_24 January 2015
P&G Purifier of water_Indovation 2015_24 January 2015
 
Chp 9
Chp 9Chp 9
Chp 9
 
Quy trinh u vo cafe voi men vi sinh rhodophos
Quy trinh u vo cafe voi men vi sinh rhodophosQuy trinh u vo cafe voi men vi sinh rhodophos
Quy trinh u vo cafe voi men vi sinh rhodophos
 
food-microbiology
food-microbiologyfood-microbiology
food-microbiology
 

Similar to Water treatment

Disinfection theory.ppt
Disinfection theory.pptDisinfection theory.ppt
Disinfection theory.pptmercynana25
 
Carbon dioxide transfer characteristics of hollow-fiber, composite membranes
Carbon dioxide transfer characteristics of hollow-fiber, composite membranesCarbon dioxide transfer characteristics of hollow-fiber, composite membranes
Carbon dioxide transfer characteristics of hollow-fiber, composite membranesTarun Shesh
 
DESIGN OF A SEWAGE TREATMENT PLANT
DESIGN OF A SEWAGE TREATMENT PLANTDESIGN OF A SEWAGE TREATMENT PLANT
DESIGN OF A SEWAGE TREATMENT PLANTRatnesh Kushwaha
 
Effluent Treatment Plant(ETP)
Effluent Treatment Plant(ETP)Effluent Treatment Plant(ETP)
Effluent Treatment Plant(ETP)Nishith Tripathi
 
water concepts in chlorine ind.
water concepts in chlorine ind.water concepts in chlorine ind.
water concepts in chlorine ind.Mohammad Abu Awwad
 
SEWAGE TREATMENT PLANT.pptx
SEWAGE TREATMENT PLANT.pptxSEWAGE TREATMENT PLANT.pptx
SEWAGE TREATMENT PLANT.pptxAthiraMenon32
 
Design criteria for Primary Clarifier.pptx
Design criteria for Primary Clarifier.pptxDesign criteria for Primary Clarifier.pptx
Design criteria for Primary Clarifier.pptxfitamadahlia2021
 
Water treatment II
Water treatment IIWater treatment II
Water treatment IILALIT SHARMA
 
Alternatives of chlorine, chlorine di-oxide(ClO2) for water treatment
Alternatives of chlorine, chlorine di-oxide(ClO2) for water treatmentAlternatives of chlorine, chlorine di-oxide(ClO2) for water treatment
Alternatives of chlorine, chlorine di-oxide(ClO2) for water treatmentRaghab Gorain
 
Water purification techniques
Water purification techniquesWater purification techniques
Water purification techniquesRashid Tk
 
Ecw 579 week 6. latest
Ecw 579 week 6. latestEcw 579 week 6. latest
Ecw 579 week 6. latestAdilah Anuar
 
Tertiary waste management ppt
Tertiary waste management pptTertiary waste management ppt
Tertiary waste management pptRajatsingh
 
Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...
Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...
Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...CRL Asia
 
Effluenttreatmentplantetp 090630115120-phpapp02
Effluenttreatmentplantetp 090630115120-phpapp02Effluenttreatmentplantetp 090630115120-phpapp02
Effluenttreatmentplantetp 090630115120-phpapp02Sashi Sharma
 
Irwa Presentation 2009
Irwa Presentation 2009Irwa Presentation 2009
Irwa Presentation 2009h20lyle
 
Water Treatment Technology
Water Treatment TechnologyWater Treatment Technology
Water Treatment TechnologyNilay Patel
 

Similar to Water treatment (20)

Disinfection theory.ppt
Disinfection theory.pptDisinfection theory.ppt
Disinfection theory.ppt
 
Carbon dioxide transfer characteristics of hollow-fiber, composite membranes
Carbon dioxide transfer characteristics of hollow-fiber, composite membranesCarbon dioxide transfer characteristics of hollow-fiber, composite membranes
Carbon dioxide transfer characteristics of hollow-fiber, composite membranes
 
DESIGN OF A SEWAGE TREATMENT PLANT
DESIGN OF A SEWAGE TREATMENT PLANTDESIGN OF A SEWAGE TREATMENT PLANT
DESIGN OF A SEWAGE TREATMENT PLANT
 
Effluent Treatment Plant(ETP)
Effluent Treatment Plant(ETP)Effluent Treatment Plant(ETP)
Effluent Treatment Plant(ETP)
 
water concepts in chlorine ind.
water concepts in chlorine ind.water concepts in chlorine ind.
water concepts in chlorine ind.
 
Acid cleaning Procedure.pdf
Acid cleaning Procedure.pdfAcid cleaning Procedure.pdf
Acid cleaning Procedure.pdf
 
Lecture on purification of water by
Lecture on purification of water byLecture on purification of water by
Lecture on purification of water by
 
SEWAGE TREATMENT PLANT.pptx
SEWAGE TREATMENT PLANT.pptxSEWAGE TREATMENT PLANT.pptx
SEWAGE TREATMENT PLANT.pptx
 
Water treatment
Water treatmentWater treatment
Water treatment
 
Design criteria for Primary Clarifier.pptx
Design criteria for Primary Clarifier.pptxDesign criteria for Primary Clarifier.pptx
Design criteria for Primary Clarifier.pptx
 
Water treatment II
Water treatment IIWater treatment II
Water treatment II
 
Week8
Week8Week8
Week8
 
Alternatives of chlorine, chlorine di-oxide(ClO2) for water treatment
Alternatives of chlorine, chlorine di-oxide(ClO2) for water treatmentAlternatives of chlorine, chlorine di-oxide(ClO2) for water treatment
Alternatives of chlorine, chlorine di-oxide(ClO2) for water treatment
 
Water purification techniques
Water purification techniquesWater purification techniques
Water purification techniques
 
Ecw 579 week 6. latest
Ecw 579 week 6. latestEcw 579 week 6. latest
Ecw 579 week 6. latest
 
Tertiary waste management ppt
Tertiary waste management pptTertiary waste management ppt
Tertiary waste management ppt
 
Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...
Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...
Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...
 
Effluenttreatmentplantetp 090630115120-phpapp02
Effluenttreatmentplantetp 090630115120-phpapp02Effluenttreatmentplantetp 090630115120-phpapp02
Effluenttreatmentplantetp 090630115120-phpapp02
 
Irwa Presentation 2009
Irwa Presentation 2009Irwa Presentation 2009
Irwa Presentation 2009
 
Water Treatment Technology
Water Treatment TechnologyWater Treatment Technology
Water Treatment Technology
 

More from Gokul Saud

Cementing Materials
Cementing MaterialsCementing Materials
Cementing MaterialsGokul Saud
 
Water Induced Disaster Risk Management
Water Induced Disaster Risk ManagementWater Induced Disaster Risk Management
Water Induced Disaster Risk ManagementGokul Saud
 
Photogrammetry- Surveying
Photogrammetry- SurveyingPhotogrammetry- Surveying
Photogrammetry- SurveyingGokul Saud
 
Contouring pdf
Contouring pdfContouring pdf
Contouring pdfGokul Saud
 
Chapter 3 classification
Chapter 3 classificationChapter 3 classification
Chapter 3 classificationGokul Saud
 
Global positioning system (gps)
Global positioning system (gps)Global positioning system (gps)
Global positioning system (gps)Gokul Saud
 
Consolidation nec
Consolidation necConsolidation nec
Consolidation necGokul Saud
 
Chapter one gis
Chapter one gisChapter one gis
Chapter one gisGokul Saud
 
Microsoft power point distribution systems [read-only]
Microsoft power point   distribution systems [read-only]Microsoft power point   distribution systems [read-only]
Microsoft power point distribution systems [read-only]Gokul Saud
 
Membrane filtration
Membrane filtrationMembrane filtration
Membrane filtrationGokul Saud
 
Hydrographic survey for std not print
Hydrographic survey for std not printHydrographic survey for std not print
Hydrographic survey for std not printGokul Saud
 
Pipe appuretenances, valves and fittings
Pipe appuretenances, valves and fittingsPipe appuretenances, valves and fittings
Pipe appuretenances, valves and fittingsGokul Saud
 
Remote sensing
Remote sensingRemote sensing
Remote sensingGokul Saud
 
Soil mecahnics ka notes
Soil mecahnics ka notesSoil mecahnics ka notes
Soil mecahnics ka notesGokul Saud
 
Chapter 9 gravity flow water supply system
Chapter 9 gravity flow water supply systemChapter 9 gravity flow water supply system
Chapter 9 gravity flow water supply systemGokul Saud
 
Numerical from-photogrammetry-and-relief-displacement-derivation
Numerical from-photogrammetry-and-relief-displacement-derivationNumerical from-photogrammetry-and-relief-displacement-derivation
Numerical from-photogrammetry-and-relief-displacement-derivationGokul Saud
 
Chapter 7 conveyance of water
Chapter 7 conveyance of waterChapter 7 conveyance of water
Chapter 7 conveyance of waterGokul Saud
 
Triangulation and trilateration pdf...
Triangulation and trilateration pdf...Triangulation and trilateration pdf...
Triangulation and trilateration pdf...Gokul Saud
 

More from Gokul Saud (19)

Cementing Materials
Cementing MaterialsCementing Materials
Cementing Materials
 
Water Induced Disaster Risk Management
Water Induced Disaster Risk ManagementWater Induced Disaster Risk Management
Water Induced Disaster Risk Management
 
Photogrammetry- Surveying
Photogrammetry- SurveyingPhotogrammetry- Surveying
Photogrammetry- Surveying
 
Contouring pdf
Contouring pdfContouring pdf
Contouring pdf
 
Chapter 3 classification
Chapter 3 classificationChapter 3 classification
Chapter 3 classification
 
Global positioning system (gps)
Global positioning system (gps)Global positioning system (gps)
Global positioning system (gps)
 
Consolidation nec
Consolidation necConsolidation nec
Consolidation nec
 
Chapter one gis
Chapter one gisChapter one gis
Chapter one gis
 
Microsoft power point distribution systems [read-only]
Microsoft power point   distribution systems [read-only]Microsoft power point   distribution systems [read-only]
Microsoft power point distribution systems [read-only]
 
Membrane filtration
Membrane filtrationMembrane filtration
Membrane filtration
 
Last day note
Last day noteLast day note
Last day note
 
Hydrographic survey for std not print
Hydrographic survey for std not printHydrographic survey for std not print
Hydrographic survey for std not print
 
Pipe appuretenances, valves and fittings
Pipe appuretenances, valves and fittingsPipe appuretenances, valves and fittings
Pipe appuretenances, valves and fittings
 
Remote sensing
Remote sensingRemote sensing
Remote sensing
 
Soil mecahnics ka notes
Soil mecahnics ka notesSoil mecahnics ka notes
Soil mecahnics ka notes
 
Chapter 9 gravity flow water supply system
Chapter 9 gravity flow water supply systemChapter 9 gravity flow water supply system
Chapter 9 gravity flow water supply system
 
Numerical from-photogrammetry-and-relief-displacement-derivation
Numerical from-photogrammetry-and-relief-displacement-derivationNumerical from-photogrammetry-and-relief-displacement-derivation
Numerical from-photogrammetry-and-relief-displacement-derivation
 
Chapter 7 conveyance of water
Chapter 7 conveyance of waterChapter 7 conveyance of water
Chapter 7 conveyance of water
 
Triangulation and trilateration pdf...
Triangulation and trilateration pdf...Triangulation and trilateration pdf...
Triangulation and trilateration pdf...
 

Water treatment

  • 1. 1 TYPES OF SEDIMENTATION TANKS 1. Quiescent or fill and draw type:  Rectangular in plan.  Water is filled, allowed for retention period of 30 to 60 hrs (normally 24 hrs) then clear water is drawn from outlet  Empty the tank and cleaning of sediment is done.  Needs more detention period, labours and supervision,  More than one tanks  Not used nowadays.
  • 2. 2 2. Continuous type: A. Horizontal Flow Type (a) Rectangular tanks with longitudinal flow
  • 3. 3 (b) Circular with radial flow i. Circular with central feed ii. Circular with peripheral feed
  • 5. 5 Surface loading or surface overflow rate (SOR) of sedimentation tank:
  • 6. 6 PROCESS OF SEDIMENTATION WITH COAGULATION 1. Feeding the coagulant Dry feeding Wet Fedding 2. Mixing of coagulant a. Mixing basin with baffle walls b. Mixing basin with mechanical means c. Mixing channels d. Hydraulic jump method e. Compressed air method f. Centrifugal pumping method 3. Flocculation 4. Sedimentation
  • 7. 7 a. Mixing basin with baffle walls i. Horizontal or round end type:
  • 8. 8 ii. Vertical or over and under type
  • 9. 9 b. Mixing basin with mechanical means
  • 11. 11
  • 13. 13 FILTER AND THEIR CLASSIFICATION 1. Slow sand filter (SSF)
  • 14. 14 a. Enclosure tank:  depth = 2.5 – 3.5 m  surface area = 10 – 2000 m2  filtration rate = 100 – 200 lph/m2  cross slope = 1 in 100 – 1 in 200 towards central drain b. Filter media: • sand layer = 90 – 110 cm thick • effective size (D10) = 0.25 – 0.35 mm (0.3 mm is common) • coefficient of uniformity (Cu) = 3 – 5. c. Base material: • 30 to 75 cm thick gravel • four layers of each about 15 cm • 3 – 6 mm, 6 – 20 mm, 20 – 40 mm and 40 – 65 mm from the top e. Appurtenances: vertical air pipes, depth controlling devices,head loss measuring device, rate maintaining devices etc
  • 15. 15 d. Under drainage system: Efficiency of SSF:  98 – 99% bacteria removal  removes turbidity up to 50 ppm  Only 20 – 25 % of color removal  not so efficient in removal of colloidal matters
  • 16. 16 2. Rapid sand filter (RSF)
  • 17. 17 a. Enclosure tank:  depth = 2.5 – 3.5 m  surface area = 10 – 50 m2  filtration rate = 3000 – 6000 lph/m2  Length width ratio = 1.25 – 1.35 b. Filter media:  sand layer = 60- 90 cm thick  effective size (D10) = 0.35 – 0.60 mm  coefficient of uniformity (Cu) = 1.3-1.7. c. Base material: • 45 to 60 cm thick gravel • four layers of each about 15 cm • 2 – 6 mm, 6 – 12 mm, 12 – 20 mm and 20 – 50 mm from the top
  • 19. 19 e. Appurtenances: Wash water trough, air compressor, rate control device, head loss indicators meters, valves etc Efficiency of RSF:  35-40 ppm turbidity removal  removes colour below 3 ppm  Less efficient in iron and manganese removal  not efficient in odour removal  Less efficient in bacteria removal (Only 80 – 90 %)
  • 20. 20 3. Pressure filter (PF) water is passed under pressure of 3 – 7 kg/cm2 through pumping  Rate of filtration of PF is 6000 – 15000 lit/hr/m2 of filter area  low efficient than RSF for the removal of color, turbidity and bacterial load  can be used for small colonies, industry and swimming pools etc.
  • 21. Difference between 21 Criteria Slow sand filter Rapid sand filter Filtration rate LPH/M2 100 – 200 3000-6000 Filter Media :sand layer (cm) 90 – 110 60-90 effective size (D10) mm 0.25 – 0.35 0.35-0.6 coefficient of uniformity (Cu) 3 – 5. 1.3-1.7 Efficiency bacteria removal 98 – 99% Less efficient (Only 80 – 90 %)
  • 22. 22 DISINFECTION  To kill pathogens  Chemicals called disinfectants Characteristics of a good disinfectants: 1.Should be able to destroy all harmful bacteria economically within the contact time and in the wide range of temperature and pH values. 2.It should not render the water toxic or impart colour and odour. 3.It should be easily available at reasonable cost. 4.It should be safe to handle and method of application should be simple. 5.It should persist in residual concentrations as safeguard recontamination.
  • 23. 23 Methods of disinfection: Chlorination • When Chlorine is used Cl2 + H2O ↔ HOCl + H+ + Cl – [Called Hydrolysis reaction occurs at 49 - 212°C] The HOCl further dissociates (ionizes) as follows HOCl ↔ H+ + OCl – [Called Ionization reaction] HOCl and OCl – penetrate cell walls and reacts with the enzyme system in the cell of micro-organism and results death of micro- organism
  • 24. 24 FORMS OF APPLICATION OF CHLORINE (a) Bleaching powder CaOCl2 ↔ Ca++ + 2 OCl – H+ + OCl – ↔ HOCl – this process is called hypochlorination (b) Chloramines H2O + Cl2↔ HOCl + H++ Cl – NH3 + HOCl ↔ NH2Cl (monochloramine) + H2O NH2Cl + HOCl ↔ NHCl2 (dichloramine) + H2O NHCl2 + HOCl ↔ NCl3 (trichloramine) + H2O (c) Chlorine gas or liquid chlorine (d) Chlorinedioxide 2NaClO2 + Cl2 ↔ 2NaCl + 2 ClO2↑
  • 25. 25 CHLORINE DEMAND AND DOSE (a) Chlorine demand Chlorine demand = Total amount of chlorine added – Amount of residual chlorine required after a specified contact period Reaction for combined available chlorine: Cl2 + H2O ↔ HOCl + H++ Cl – NH3 + HOCl ↔ NH2Cl (monochloramine) + H2O NH2Cl + HOCl ↔ NHCl2 (dichloramine) + H2O NHCl2 + HOCl ↔ NCl3 (trichloramine) + H2O (b) Chlorine dose Quantity of chlorine required to be added to water to leave 0.2 mg/l or ppm of freely available residual chlorine after 10 minutes of contact period
  • 26. 26 FORMS OF CHLORINATION 1. Plain chlorination or simple chlorination: To raw water 2. Pre-chlorination: Before treatment 3. Post chlorination: After treatment 4. Double or multiple chlorination: Two or more point 5. Super chlorination: Application beyond break point 6. De-chlorination Removing chlorine 7. Break point chlorination or free residual chlorination:
  • 27. 27 7. Break point chlorination or free residual chlorination:
  • 28. 28 FACTORS AFFECTING BACTERIAL EFFICIENCY OF CHLORINE 1.Turbidity: low efficient 2.Presence of metallic compound: Efficiency is decreased. 3.Ammonia compound: Efficiency is decreased 4.pH value of water: If pH is high in water, efficiency is low 5. Temperature: If temperature decreased, efficiency decreased. 6.Time of contact: time of contact should be at least 30 minutes. 7.Type, condition and concentration of micro-organism: Efficiency low if the favorable condition for bacteria is available and concentration of bacteria is high.
  • 29. 29 WATER SOFTENING • Process of removing hardness • Purpose: To remove Hardness A. Removal of temporary hardness: (a) Boiling: It is costlier and not used in public water supply. Ca(HCO3)2 CaCO3↓ + CO2↑ + H2O Mg(HCO3)2 MgCO3↓ + CO2 ↑+ H2O (b) Adding lime: Ca(HCO3)2 + Ca(OH)2 → 2CaCO3↓ + 2H2O Mg(HCO3)2 + Ca(OH)2 → CaCO3↓ + MgCO3↓ + 2H2O
  • 30. 30 A. Removal of permanent hardness: a. Lime soda process: CO2 + Ca(OH)2 = CaCO3↓ + H2O Ca(HCO3)2 + Ca(OH)2 = 2CaCO3↓ + 2H2O Mg(HCO3)2 + Ca(OH)2 = CaCO3↓ + MgCO3 + 2H2O MgCO3 + Ca(OH)2 = Mg(OH)2↓ + CaCO3↓ MgSO4 + Ca(OH)2 = Mg(OH)2↓ + CaSO4 CaSO4 + Na2CO3 = CaCO3↓ + Na2SO4 MgCl2 + Ca(OH)2 = Mg(OH)2↓ + CaCl2 CaCl2 + Na2CO3 = CaCO3↓ + 2NaCl MgCl2 + Na2CO3 = MgCO3 + 2NaCl           +      →           + 2NaCl SONa 2NaHCO Z Mg Ca Cl SO )(HCO Mg Ca ZNa 42 3 2 4 23 2 b. Permutit Process:
  • 32. 32 C. Demineralization or deionization process: Regeneration of zeolite: 22 Cl Mg Ca ZNa2NaClZ Mg Ca       +→+                + +      →           + 2HCl SOH 2COO2H R Mg Ca Cl SO )(HCO Mg Ca RH 42 22 2 4 23 2 Regeneration of hydrogen exchanger:                 +→+           2 4 2 42 2 Cl/Cl SO 2Na Mg Ca RH HCl SOH R Na Mg Ca
  • 33. 33 MISCELLANEOUS TREATMENT A. Aeration: (A) Aeration (B) Removal of iron and manganese (C) Removal of colour odour and taste Purpose of aeration: 1. To make water fresh by absorbing oxygen from air. 2. To release dissolved gases (CO2, H2S etc) to atmosphere. 3. To remove bad taste and odour. 4. To reduce corrosiveness of water. 5. To precipitate Fe and Mn to some extent by oxidizing. 6. To kill harmful bacteria to some extent. 7. To mix mixing chemicals to water.
  • 34. 34
  • 35. 35 Methods of aeration: Free fall or gravity aerators:
  • 36. 36
  • 37. 37 Methods of aeration: Free fall or gravity aerators: Mechanical aerators:
  • 38. 38 Free fall or gravity aerators:
  • 39. 39
  • 40. 40
  • 41. 41 B. Removal of iron and manganese: Effect: i. Produce taste, odour and brown red colour. ii.Stains on clothes, corrosion and clogging of pipes by accumulation of precipates. iii.Causes difficult in various industrial process. Purpose: Removal of iron and manganese Methods: (a) By aeration (b) By adding lime (c) Passing over manganese zeolite
  • 42. 42 (a) By aeration: In this case aeration is done before sedimentation. Fe: 4Fe + O2 + 10 H2O → 4Fe(OH)3 ↓ + 8H Fe(HCO3)2 : Fe(HCO3)2 + 2H2O → FeO + 2CO2 + 3H2O 4FeO + O2 → 2Fe2O3 Fe2O3 + 3H2O → 2Fe(OH)3 ↓ Mn: 6Mn + 3O2 + 6H2O → 6MnO2 ↓ + 12H
  • 43. 43 C. Removal of colour, odour, taste: Purpose: Removal of colour, odour and taste Methods: (a) By aeration (b) By activated carbon treatment • Activated carbon is manufactured by heating saw dust, paper mill waste etc. at 500°C in a closed vessel in controlled condition of burning at 800°C. • readily available in market in powder or granular form • absorbs organic matters and removes colour, odour and taste. (c) Using copper sulphate: in swimming pools
  • 44. SODIS method is very easy to apply: A transparent PET bottle is cleaned with soap. Then, the bottle is filled with water and placed in full sunlight for at least 6 hours. The water has then been disinfected and can be drunk.
  • 47. 47
  • 48. 48
  • 49. BIO SAND FILTER • (BSF) is a point-of-use water treatment system adapted from traditional slow sand filters. • Bio sand filters remove pathogens and suspended solids from water using biological and physical processes that take place in a sand column covered with a bio film. • BSFs have been shown to remove heavy metals, turbidity, bacteria, viruses and protozoa. • BSFs also reduce discoloration, odor and unpleasant taste. • Studies have shown a correlation between use of BSFs and a decrease in occurrence of diarrhea because of their effectiveness, ease of use, and lack of recurring costs, bio sand filters are often considered appropriate technology in developing countries.
  • 50.
  • 51.
  • 52.
  • 53.
  • 54.
  • 55. How Well Does the Bio sand Filter Work? • Water naturally contains many living things. Some are harmless and others can make people sick. Living things that cause disease are also known as pathogens. They are sometimes called other names, such as microorganisms, microbes or bugs, depending on the local language and country. • There are four different categories of pathogens that are : bacteria, viruses, protozoa and helminths. • Turbid water looks cloudy, dirty or muddy and is caused by sand, silt and clay that are floating in the water. Drinking turbid water will not make people sick by itself. • However, viruses, parasites and some bacteria can sometimes attach themselves to the suspended solids in water. • This means that turbid water usually has more pathogens so drinking it increases the chances of becoming sick
  • 56. 56 CHAPTER 7: INTRODUCTION TO CONVEYANCE • Transportation of water to treatment plant or reservoir or distribution through conduits. • Transmission: Source – TP – Reservoir • Distribution: Reservoir – Users Tap • Conduits: A. Gravity: Open channel flow Canals, aqueducts, tunnels B. Pressure Pipes, pressure tunnels, pressure aqueducts etc.
  • 57. 57 PIPE, PIPE MATERIALS AND PIPE TYPES Pipe: • Circular conduit where fluid flows under pressure • Designed to carry external and internal loads Requirement of good pipe: • Withstand external, internal and temperature stresses • Smooth for minimum frictional losses • Durable • Light • Noncorrosive • Cheap • Easy joint
  • 58. 58 Pipe types as per materials:
  • 59. 59 (a) Cast Iron (CI) Pipe: • Manufactured by sand molding or centrifugal method • Standard 1.8 m length but up to 3m for smaller diameter • 50 mm to 1.2 m dia. Advantages: Easy to join, can withstand high pressure, resistance to corrosion, long life (> 100 yrs), durable, strong and moderate in cost, joined by flanged or Spigot and socket joint, low maintenance cost. Disadvantages: Brittle and very heavy so difficult to transport and may be expensive. Suitability: Suitable for distribution system.
  • 60. 60 (b) Wrought Iron (WI) Pipe: • Manufactured by rolling the flat plates of metal to proper diameter and welding to the edges Advantages: Strong, light weight, can withstand high pressure (400 m) and cheaper than CI pipes Disadvantages: It can’t withstand external load and when there is no water inside, liable to corrosion and costly to maintain. It is costlier than CI pipes Suitability: Occasionally used for main lines where pressure is high
  • 61. 61 (c) Steel Pipe: • Manufactured by WI or mild steel which are galvanized by providing a protective coating of zinc on inner and outer surface Advantages: It is cheap, light, easy in handling and transport, easy in joining with screwed socket joints and 20 years of life, resistant to corrosion when exposed to atmosphere Disadvantages: may get corroded by acidic and alkaline waters and liable to incrustation. Suitability: main lines where pressure is high and when pipe is exposure in open atmosphere
  • 62. 62 (d) Galvanized iron (GI) pipes: • Manufactured similar as WI pipes • 15,20,25,32,40,50,63,75,90,110,125,150, 200 mm inner dia Advantages: Light in weight, easy in transport, handling, cutting, threading, working, joining, and gives neat appearance, joined couplings or screwed socket joint. Disadvantages: Costly, corrosive and less durable than CI pipes Suitability: Inside plumbing in buildings but not used nowadays due to high cost.
  • 63. 63 (e) Concrete (GI) pipes: • Made of cement concrete (precast or cast in site) Advantages: Withstand 150 m head of water, resist corrosion and life is above 75 years, maintenance cost is low, least thermal expansion, can be laid under water and resist normal traffic load Disadvantages: Precast type is heavy to handle and transport, concrete pipes can’t resist high pressure and difficult to repair, it may be affected by acids and alkali and salty waters, difficult to join and liable to leak due to porosity Suitability: Where water does not flow under pressure (i.e. sewerage system)
  • 64. 64 (f) Asbestos cement (AC) pipes: • Made of mixture of cement and asbestos fibers Advantages: not affected by salt water and corrosive materials, smooth, light so easy in handling Disadvantages: Affected by alkali and acid and also brittle so costlier in transport. Suitability: Small size distribution pipes
  • 65. 65 (g) Wooden pipes: • made of wood by making channels or boring at center and used in ancient times • not used in water supply nowadays (h) Vitrified clay Pipes: • made of vitrified clay so has smooth surface • not used in water supply nowadays (i) Lead and copper Pipes: • Copper pipe is made of copper and can resist corrosion even if water contains some acids and expensive so not used in water supply nowadays • Leads are soluble in water so lead pipe causes lead poisoning hence it is not used in water supply nowadays.
  • 66. 66 (f) Plastic Pipes: • Made of Plastic and common in nowadays • it is corrosion resistant, light in weight and economical Advantages: Light, cheap, available in longer length, electrical insulation, corrosion free, life correspond to GI Disadvantages: Less resistant to hot water, may impart smell to water, can be easily cut. Suitability: All water sypply systems
  • 67. 67 Types: 1. Low density polyethylene (LDPE) pipes: Used in electrical wiring 2. High density polyethylene (HDPE)pipes 3. Polyvinyl chloride (PVC) pipes: 4. Unplastisized Polyvinyl chloride (UPVC) pipes: 5. Poly Propylene Random (PPR) Pipes: Plastic Pipes
  • 68. 68 LAYING OF PIPES 1.Preparation of detailed maps: 2.Locating proposed alignment of pipeline on the ground: 3.Location of pipes with respect to ground surface during laying 4.Excavation of trench: 5.Dewatering of trench: 6.Lowering the Pipes: 7.Joining pipes: 8.Testing of pipes: 9.Back filling and disinfection before first use:
  • 69. 69
  • 71. 71
  • 72. 72
  • 73. 73
  • 74. 74
  • 75. 75 CHAPTER 8: VALVES AND FITTINGS (a) Sluice or gate or cutoff valve (b) Reflux or check or non-return valve (c) Safety or pressure relief valve (d) Air valve or air relief valve (e) Drain or scour or blow off valve : Ordinary sluice valve to remove silt deposit (f) Butterfly valve and globe valve Devices used to control the flow of water, regulate pressures, release air, prevent back flow etc
  • 76. 76
  • 77. 77
  • 78. 78
  • 79. 79 FIRE HYDRANT:  Devices used for tapping water from mains for the fire extinguishing, street washing, watering gardens, flushing sewer lines etc.  Provided at all road junctions & every 100 – 300 m apart.  For tapping water, the hose is connected to the hydrant and if necessary the engine is used to increase head.  It should be cheap, easily connectable & detachable to the hose pipe and able to give sufficient water. It may be of post type or flush type.
  • 80. 80
  • 82. 82
  • 83. 83
  • 84. 84 CHAPTER 9: PLANNING OF GRAVITY WATER SUPPLY • Need identification of scheme • After need identification, mass meeting is called, prioritize is done and then scheme acquisition form is filled up and submitted to VDC, DDC and divisional district water supply office • With feasibility study report the schemes are forwarded from divisional office thru regional office to department of water supply and sewerage (DWSS) • After obtaining scheme acquisition form list from all 75 districts , budget ceiling is prepared for forthcoming fiscal year by DWSS and forward to ministry of concern. • The ministry approves ceiling consulting with National planning commission then distributed to DWSS and district offices for implementation
  • 85. 85 • After obtaining approved budget ceiling, detailed survey is carried out. • Detail survey  horizontal and vertical control and  questionnaire • Analysis based on detail survey, the design, drawing, estimating and costing is done and final report is prepared. • Water Users Committee (WUS) is formed and trained in agreement with WUC or implementation agency • After agreement, construction is carried out and it is handover to the WUC. • WUC are responsible for regular maintenance.