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Water treatment process
screening
aeration
Plain
sedimentation
Sedimentation
with coagulation
Filtration
Disinfection
Softening
Water treatment process
SCREENING
• screens are used to remove the floating matters. This
process is called screening.
• screens are generally placed at 30-60º angle, to reduce the
velocity of flow and increase the cross-sectional area.
• The velocity of flow, sec/0.175.0 mvf 
screens
Coarse screens
Size: 25-75 mm
Fine screens
size: 10-3 mm
screening
aeration
Plain
sedimentation
Sedimentation
with coagulation
Filtration
Disinfection
Softening
Water treatment process
• Aeration brings water and air in close contact in order
to remove dissolved gases (such as carbon dioxide)
• It oxidizes dissolved metals such as iron, hydrogen
sulfide, and volatile organic chemicals.
• Oxygen is added to water through aeration.
Air diffusion method
Methods of Aeration
Cascade method
Trickling plates method
Spray nozzle method
screening
aeration
Plain
sedimentation
Sedimentation
with coagulation
Filtration
Disinfection
Softening
Water treatment process
SEDIMENTATION
Sedimentation is a process in which the suspended materials or
solids are made to settle by gravity under still water condition
Sedimentation
Plain Sedimentation
(the impurity is
separated by natural
forces)
Sedimentation with
coagulation (impurity
is removed by some
chemicals)
Continuous Flow Rectangular sedimentation tank
Baffles walls
Radial flow sedimentation tank
Hopper Bottom Continuous Flow Sedimentation Tank
Design of Sedimentation Tank
The design of sedimentation tank is done based on volume of
water to be treated.
STEPS: 1. the height of tank H= 3.5 – 6.0m
min/30.015.0 mvf 2.Velocity of flow:
3. Capacity of tank:
“Detention period: the time between entry and exit of a fluid particle
in sedimentation tank.”
hourst
hourst
d
d
42
84


Q
C
td 
For plain sedimentation:
For sedimentation with coagulation :
Where, =detention time
C= capacity of tank
Q= discharge per hour
dt
4. The L:B is generally taken as 4:1
mD
mB
60
12


The diameter of circular tank
Width of rectangular tank
**Detention time for vertical flow circular tank:
 
Q
HDD
td
785.0011.02


Where, D=dia of tank
H = height of tank
screening
aeration
Plain
sedimentation
Sedimentation
with coagulation
Filtration
Disinfection
Softening
Water treatment process
It is a process in which an insoluble flocculent precipitate is formed
by adding certain chemicals for absorbing colloidal matter.
Coagulants: the chemicals added to water for forming insoluble
precipitate during coagulation process . Some coagulants are:
1. Aluminum Sulphate (Alum):
It is reactive in basic water.
In acidic water lime is added with ALUM.
Chemical Reaction of Alum:
1. When water is Basic:
     
224
323242
6183
2318.
COOHCaSO
OHAlHCOCaOHSOAl


precipitate
2.When water is acidic:
      OHCaSOOHAlOHCaOHSOAl 2432242 1832318. 
precipitate
• For complete reaction the pH of water should be 6-8.5
• 0.03-0.13 gm Alum is added in 1lit of water
Feeding Devices for Coagulation
1. Dry feed device:
Dey feeding device (a) by toothed wheel, (b) by helical wheel
2. Solution feed device
Conical plug and float device
Flocculation
The formation od floc in sedimentation tank when coagulants
are added into the sedimentation tank is called flocculation
• After flocculation water enters the settling tank which is called
clarifier
• In this operation the floc which has been formed above is
allowed to settle
Optimum Dose Required For Coagulants:
It is determined by Jar Apparatus Test
1.Water is taken in every
jar
2.Coagulent is added in jar
in varying amount.
3.The quantity of
coagulant in each jar is
noted
4.All the paddles are
rotated at 30-40 rpm for
10min.
5. After this speed is
reduced and paddles are
rotated for 20*-30min.
6. The rotation of paddle
is stooped and floc
formed In ech jar is noted
and allowed to settle.
7. The dose of coagulant
which gives best floc is
the optimum dose.
screening
aeration
Plain
sedimentation
Sedimentation
with coagulation
Filtration
Disinfection
Softening
Water treatment process
“Filtration is process of passing water through bed of sand or other
granular material.”
• Filters are used for removing bacteria, color, taste, and odour.
• 95-98% suspended impurities are removed by sand filtration
following action takes place when water is filtered by sand media.
Mechanical Straining
Sedimentation and absorption
Biological action
Electrolytic action
Filters
rapid sand filter
Gravity type
Pressure type
Slow sand
(rate of flow is 1/20th or
less of rapid sand filter)
Slow Sand Filter
It is consist of following parts:• It is rectangular air tight chamber. The floor has bed slope of 1 in 100 to 1 in
200 towards the central drain.
Enclosure Tank:
• It is 90-110cm thick. Sand size = 0.2-0.3 mm and Cu=2-3.
Filter Media:
• It consist of three layers, top layer of sand
• Bottom layer of coarse sand
• gravel
Base Material:
• It is below coarse layer which collects filtered water and deliver it to
reservoir.
Under drain system
• Head loss devices, maintaining consistent rate of low devices.
appurtenances
Slow Sand Filter
Filter media description :
top sand layer thickness = 75-
90cm size = 0.2-0.3mm
Bottom sand layer, thickness
=30cm, size= 0.3-2 mm
Lowermost gravel layer, thickness
= 30 cm, size= 2-45mm.
daymv /6.34.2 
it effectively removes 98-99% bacteria of
raw water.
It can reduce turbidity upto 1NTU
• Depth= 2.5 to 3.5m, surface area= 20-50 sq.m
Enclosure Tank:
• Sand size = 0.35-0.6, Cu=1.5.
Filter Media:
• It consist of three layers, top layer of sand
• Bottom layer of coarse sand
• gravel
Base Material:
• It is below coarse layer which collects filtered water and deliver it to
reservoir.
Under drain system
• Wash water through, Air compressor, rate control device.
appurtenances
Gravity Sand Filter
Rapid Sand Filter (gravity type)
• It is only suitable when
Turbidity of water is less
than 30-40ppm.
• The filtration rate is
40000lit/m2/day
Rapid Sand Filter (pressure type)
• The pressure may vary from 3 to 7
kg/sq.m
• Thickness of filter is 50-60cm and size of
sand is 0.35-0.6mm
• The rate of filtration varies from 6000-
15000 m3/m2/hour.
screening
aeration
Plain
sedimentation
Sedimentation
with coagulation
Filtration
Disinfection
Softening
Water treatment process
The process of killing the infective bacteria from the water and
making it safe to user is called disinfection
Physical Methods
Boiling: for 15-
20min.
Ultra-voilet ray
Chemical
Methods
Chlorination
Bromine and Iodine
Potassium
permanganate
Ozone
Excess lime
treatment
Chlorination: it is applied in following forms:
• It is a process when other
treatment is not required.
• 0.8mg Cl per lit of water is required
Plain
Chlorination
• 1-2 mg Cl per liter of water is
required
Super
chlorination
• It is process of removing Cl from
waterDechlorination
screening
aeration
Plain
sedimentation
Sedimentation
with coagulation
Filtration
Disinfection
Softening
Water treatment process
Temporary
Hardness
By boiling of
water
Lime
process(lime is
added to water)
Permanent
Hardness
Lime soda
process
Zeolite process
Methods of softening of water
Zeolite Process:
• Zeolite is complex silicate of zeolite, sodium and aluminum.
• It is based on ion exchange process.
• the salt od calcium and magnesium present in water converts
to sodium salt
The reactions are as follows:
   
   
   
   
    32232323
42232324
2232322
42232324
32232324
CONaSiOMgAlSiOAlNaMgCO
SONaSiOMgAlSiOAlNaMgSO
ClNaSiOCaAlSiOAlNaCaCl
SONaSiOCaAlSiOAlNaCaSO
CONaSiOCaAlSiOAlNaCaSO






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Water treatment process

  • 2.
  • 4. SCREENING • screens are used to remove the floating matters. This process is called screening. • screens are generally placed at 30-60º angle, to reduce the velocity of flow and increase the cross-sectional area. • The velocity of flow, sec/0.175.0 mvf 
  • 5. screens Coarse screens Size: 25-75 mm Fine screens size: 10-3 mm
  • 7. • Aeration brings water and air in close contact in order to remove dissolved gases (such as carbon dioxide) • It oxidizes dissolved metals such as iron, hydrogen sulfide, and volatile organic chemicals. • Oxygen is added to water through aeration.
  • 8. Air diffusion method Methods of Aeration Cascade method Trickling plates method Spray nozzle method
  • 10. Sedimentation is a process in which the suspended materials or solids are made to settle by gravity under still water condition Sedimentation Plain Sedimentation (the impurity is separated by natural forces) Sedimentation with coagulation (impurity is removed by some chemicals)
  • 11. Continuous Flow Rectangular sedimentation tank Baffles walls
  • 13. Hopper Bottom Continuous Flow Sedimentation Tank
  • 14. Design of Sedimentation Tank The design of sedimentation tank is done based on volume of water to be treated. STEPS: 1. the height of tank H= 3.5 – 6.0m min/30.015.0 mvf 2.Velocity of flow: 3. Capacity of tank: “Detention period: the time between entry and exit of a fluid particle in sedimentation tank.” hourst hourst d d 42 84   Q C td  For plain sedimentation: For sedimentation with coagulation : Where, =detention time C= capacity of tank Q= discharge per hour dt
  • 15. 4. The L:B is generally taken as 4:1 mD mB 60 12   The diameter of circular tank Width of rectangular tank **Detention time for vertical flow circular tank:   Q HDD td 785.0011.02   Where, D=dia of tank H = height of tank
  • 17. It is a process in which an insoluble flocculent precipitate is formed by adding certain chemicals for absorbing colloidal matter. Coagulants: the chemicals added to water for forming insoluble precipitate during coagulation process . Some coagulants are: 1. Aluminum Sulphate (Alum): It is reactive in basic water. In acidic water lime is added with ALUM.
  • 18. Chemical Reaction of Alum: 1. When water is Basic:       224 323242 6183 2318. COOHCaSO OHAlHCOCaOHSOAl   precipitate 2.When water is acidic:       OHCaSOOHAlOHCaOHSOAl 2432242 1832318.  precipitate • For complete reaction the pH of water should be 6-8.5 • 0.03-0.13 gm Alum is added in 1lit of water
  • 19. Feeding Devices for Coagulation 1. Dry feed device: Dey feeding device (a) by toothed wheel, (b) by helical wheel
  • 20. 2. Solution feed device Conical plug and float device
  • 21. Flocculation The formation od floc in sedimentation tank when coagulants are added into the sedimentation tank is called flocculation • After flocculation water enters the settling tank which is called clarifier • In this operation the floc which has been formed above is allowed to settle
  • 22. Optimum Dose Required For Coagulants: It is determined by Jar Apparatus Test 1.Water is taken in every jar 2.Coagulent is added in jar in varying amount. 3.The quantity of coagulant in each jar is noted 4.All the paddles are rotated at 30-40 rpm for 10min. 5. After this speed is reduced and paddles are rotated for 20*-30min. 6. The rotation of paddle is stooped and floc formed In ech jar is noted and allowed to settle. 7. The dose of coagulant which gives best floc is the optimum dose.
  • 24. “Filtration is process of passing water through bed of sand or other granular material.” • Filters are used for removing bacteria, color, taste, and odour. • 95-98% suspended impurities are removed by sand filtration following action takes place when water is filtered by sand media. Mechanical Straining Sedimentation and absorption Biological action Electrolytic action
  • 25. Filters rapid sand filter Gravity type Pressure type Slow sand (rate of flow is 1/20th or less of rapid sand filter)
  • 26. Slow Sand Filter It is consist of following parts:• It is rectangular air tight chamber. The floor has bed slope of 1 in 100 to 1 in 200 towards the central drain. Enclosure Tank: • It is 90-110cm thick. Sand size = 0.2-0.3 mm and Cu=2-3. Filter Media: • It consist of three layers, top layer of sand • Bottom layer of coarse sand • gravel Base Material: • It is below coarse layer which collects filtered water and deliver it to reservoir. Under drain system • Head loss devices, maintaining consistent rate of low devices. appurtenances
  • 27. Slow Sand Filter Filter media description : top sand layer thickness = 75- 90cm size = 0.2-0.3mm Bottom sand layer, thickness =30cm, size= 0.3-2 mm Lowermost gravel layer, thickness = 30 cm, size= 2-45mm. daymv /6.34.2  it effectively removes 98-99% bacteria of raw water. It can reduce turbidity upto 1NTU
  • 28. • Depth= 2.5 to 3.5m, surface area= 20-50 sq.m Enclosure Tank: • Sand size = 0.35-0.6, Cu=1.5. Filter Media: • It consist of three layers, top layer of sand • Bottom layer of coarse sand • gravel Base Material: • It is below coarse layer which collects filtered water and deliver it to reservoir. Under drain system • Wash water through, Air compressor, rate control device. appurtenances Gravity Sand Filter
  • 29. Rapid Sand Filter (gravity type) • It is only suitable when Turbidity of water is less than 30-40ppm. • The filtration rate is 40000lit/m2/day
  • 30. Rapid Sand Filter (pressure type) • The pressure may vary from 3 to 7 kg/sq.m • Thickness of filter is 50-60cm and size of sand is 0.35-0.6mm • The rate of filtration varies from 6000- 15000 m3/m2/hour.
  • 32. The process of killing the infective bacteria from the water and making it safe to user is called disinfection Physical Methods Boiling: for 15- 20min. Ultra-voilet ray Chemical Methods Chlorination Bromine and Iodine Potassium permanganate Ozone Excess lime treatment
  • 33. Chlorination: it is applied in following forms: • It is a process when other treatment is not required. • 0.8mg Cl per lit of water is required Plain Chlorination • 1-2 mg Cl per liter of water is required Super chlorination • It is process of removing Cl from waterDechlorination
  • 35. Temporary Hardness By boiling of water Lime process(lime is added to water) Permanent Hardness Lime soda process Zeolite process Methods of softening of water
  • 36. Zeolite Process: • Zeolite is complex silicate of zeolite, sodium and aluminum. • It is based on ion exchange process. • the salt od calcium and magnesium present in water converts to sodium salt The reactions are as follows:                     32232323 42232324 2232322 42232324 32232324 CONaSiOMgAlSiOAlNaMgCO SONaSiOMgAlSiOAlNaMgSO ClNaSiOCaAlSiOAlNaCaCl SONaSiOCaAlSiOAlNaCaSO CONaSiOCaAlSiOAlNaCaSO     