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Purification of Water
Purification of water on Large scale
 Storage
 Filtration
 Disinfection/Chlorination
Purification of water comes under two heading:
Small scale
Storage
 Physical:
 Increase water quality
 Suspended particles (90%) settles down
 Allow the penetration of light and easy filtration
 Chemical:
Oxidation of organic matter by microbes
 Decreases free ammonium
 Increases nitrates
Results in natural purification
 Biological:
Pathogenic microbes gradually die out
 In river water 90% decrease in bacterial counts in 5-7 days
 Optimum storage period 10-14 days if longer
• Aquatic plants grow causing bad smell and colour
Purification of water on Large scale
Filtration:
98-99% microbes removed
 Biological or slow sand filter
 Mechanical or rapid sand filter
Supernatant water
Bed of graded sand
Under drainage system
Filter control valves
Elements of slow sand filter
Biological or slow sand filter
Supernatant Water:
 Depth 1.0-1.5 meter – maintained at constant level
 Purpose:
 Consistent HEAD of water to counter resistance
 Waiting period (3-12 Hrs)
 Partial purification
Sedimentation
Oxidation
Particle agglomeration
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Coarse
gravel
Fine
gravel
Coarse
sand
Fine
sand
Perforated pipes
Section of Filter Bed
Sand bed:
 Most important part of filtre
1.2 meter
 Quality of sand
Round with 0.15 – 0.35 cms diameter
Clean & free form clay, organic matter
 Sand bed is supported with graded gravels
• The sand bed presents large surface area
 13 meter = 15,000 M2
• Slow passage of water – 2 Hrs or more
Mechanical straining
Sedimentation
Adsorption
Oxidation
Bacterial action
Flow rate: 0.1 – 0.4 m3/h/m2 surface area
Vital layer:
Schmutzdecke / Zoogleal/Biological Layer
• Slimy, gelatinous layer containing thread-like algae and other
microscopic life forms
• Formation of Vital Layer is known as RIPENING of Biologica Filter
2 – 3 cms thick when fully formed
Heart of Filter
 Until formation of Vital layer, water is wasted
• Removes organic matter
• Traps bacteria
• Oxidizes ammoniacal nitrogen into nitrates
Bacteria free water
Under drainage system:
• Porous, perforated pipes for drainage of water supports
Supernatant water
Sand bed
Filter Box:
• Open rectangular Box – 2.5 to 4.0 meters deep
• May be below ground
Supernatant Water : 1 – 1.5 M
Sand bed : 1.2 M
Gravel support : 0.30 M
Filter bottom : 0.16 M
Filter Control: Venturi meter
 To control the flow of water and maintain water head
Filter Cleaning:
When the valve has to be kept fully open, cleaning is advised
Scrap top of the vital layer to 1-2 cms depth
After about 20 – 30 scrapings, new bed should be constructed
When bed height is about 0.5 – 0.8 M, construct new bed
Advantages:
 Simple to construct & operate
 Cheaper than Rapid Sand filters
 Very good quality water –
 Physically
 Chemically
 Bacteriologically
Total bacterial count – 99.9 to 99.99% reduced
E. Coli count – 99.0 to 99.9% reduction
Rapid sand Filter
or
Mechanical Filter
1885 – First Filter in USA
Types
Pressure
Gravity
Mixing
Chamber
Flocculation
Chamber
Sedimentation
Tank
Filters
Clear
Water
Storage
Chlorination
Alum
To Consumer
Coagulation:
Alum 5 – 40 mg/lit water
Depends on
Turbidity & Color
Temperature
pH
Rapid mixing:
 Violent mechanical mixing
 Rapid distribution of alum
Flocculation:
Slow, gentle mechanical stirring for about 30 min
Thick floccules of aluminium hydroxide
Sedimentation:
Stored for about 2-6 hrs for settling down of the floccules
At least 95% of the precipitate must settle down
Regular cleaning of the tank
Contains impurities & bacteria
Filtration:
Filter Bed:
 Surface area 80-90 m2 (900 ft2)
 Sand: 0.6-2 mm in size
1 meter (2.5-3 ft) depth
 Gravel: 30-40 cm (1-1.5 ft)
 Filtration rate: 5-15 m3/m2/hr
 Water: 1-1.5 meter (5-6 ft)
When HEAD loss is 7-8 ft, the Filter is cleaned
Back Washing
Advantages
 No preliminary storage needed
 Filter beds occupy less space
 40-50 times faster than Biological Filter
 Washing is easy
 Flexibility in operation
Rapid sand Slow sand
1. Space Little Large
2. Filtration rate 5-15 m3/m2/hr 0.1-0.4m3/m2//hr
3. Sand size 0.6-2 mm 0.15-0.35 mm
4. Prelim treatment Chemical coagulation Sedimentation
5. Washing Back washing Scrapping
6. Operation Highly skilled Less skilled
7. Turbidity Good Good
8. Colour Good Fair
9. Removal of Bacteria 98-99% 99.9-99.99%
Disinfection/Chlorination
of water
Supplement and not substitute of filtration
 Kills pathogenic bacteria
 No effect on certain viruses:
 Polio, Hepatitis
 Spores need higher dose
Along with germicidal effect it oxidizes Fe, Mn, H2S
Eliminates some taste/odour producing substances
Controls algae and slime organisms
Aids coagulation
H2O + Cl2  HOCl + HCl
Neutralized with water alkalinity
HOCl  H + OCl
 Disinfectant action is because of HOCl and OCl
 HOCl 70-80 times more active than OCl
 Best action at pH 7.0  HOCl predominates
 Action of Cl2 at pH 8.5 is unreliable
90% HOCl  OCl
Action:
pH of water
6.0-7.5
Principle:
 Water should be clear, free from turbidity
 Chlorine demand should be estimated
 Contact period  60 min
 Minimum concentration of free Cl2:
0.5 mg/lit for one hour
 Correct dose:
Cl2 demand + Free Cl2
 Difference between amount of Cl2 added and amount of residual Cl2
at the end of specific period of contact (60 min) at a given
temperature and pH of water
 Amount of Cl2 needed to destroy bacteria and oxidize organic matter
and ammonical substances present in water
Chlorine demand:
Break Point:
The point at which free chlorine starts appearing in water
The point at which Chlorine Demand of water is met
Method of Chlorination
Chlorine gas:
First choice, replaced other Cl2 derivatives
- Cheap
- Quick in action
- Efficient
- Easy to apply
Chloramine:
 Loose compound of Cl2 and NH3
 Decrease tendency to give chlorinous taste
 Increase persistent residual Cl2
 Slower action as compare to Cl2 gas
Perchloron:
- Ca-compound with 60-70% of Cl2
Break point chlorination/Free residual chlorination - Only reliable method of
chlorination
Superchlorination:
- It is followed by dechlorination
- Used in heavily polluted water
Addition of Cl2 till all organic matter present in water is completely oxidized
and a little amount of free chlorine is left in water
Orthotolidine test
 Developed in 1918
 Detects both free & Combined chlorine
O-tolidine (AR) solution in HCl (10%)
Yellow color – proportional to concentration
 Reacts instantaneously with free chlorine
 Reacts slowly with bound chlorine
 0.1 ml OT reagent + 1.0 ml Water
 Take reading within 10 seconds
 Color appearing after 15-20 min – due to bound Cl2
Orthotolidine-Arsenate (OTA) test
 Modification to eliminate reactions on account of interfering substances such as iron,
manganese etc
Ozonization:
 Powerful oxidizing agent
 Removes undesirable odour, colour
and taste
 Inactivates viruses
1906  France  First ozone treatment plant
 No residual effect

 0.2 to 1.5 mg/lit water
Advantages Disadvantages
Great potential usefulness
UV-irradiation:
 Effective against most water containing microbes, not used on large scale
120 mm thick water table
200-295 nm wavelength
No residual taste, odour
Very short exposure
Over-exposure has no side effect
No foreign substance introduced
Very expensive
No residual activity
Color/turbidity in water effectiveness
No rapid test to detect effectiveness
Advantages Disadvantages
Small-scale purification
House:
Boiling:
 Rolling boil (5-10’)
 Taste altered
 No residual effect
Chemical disinfection:
Bleaching powder:
Chlorinated lime
CaOCl2 –unstable, 33% available Cl2
Mixed with lime 0.5 mg/lit
Chlorine tablets:
- Costly, good for small scale use
- 1 tab (0.5 gm)  20 lit water
Iodine:
2% solution  2 drops/lit  20-30’
- High cost
- Physiological activity
Chlorine solution:
4 kg Bleaching Powder (5% solution of Cl2)
20 lit Water (25% Cl2)
Water filters:
- Chamberland filters
- Berkfeld filters
Disinfection of wells
3.14 x d2 x h
4
1. Volume of water (lit.)
2. Amount of bleaching powder
x 1000
Volume :
d: Diameter in meter
h: Depth of water table
in meter
2.5 g/1000 lits water (0.7 mg Cl2/lit of H2O)
Bleaching powder :
Dissolve in water and discard sediment
- Add this solution to water in well
- Leave for 1 hour, Test by OTA
Discard Lime  Hardness
Double Pot Method
 Continuous release of Cl2
 One meter below water level
• Satisfactory for 2-3 weeks
• with 4,500 lits water in the well
• 360-450 lit/day consumption
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Bleaching Powder
&
Coarse Sand
-- -- -- --
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-- --
-- --
1 cm Hole
1 cm Hole
Purification-of-Water.ppt

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Purification-of-Water.ppt