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RAM NAIK. M 4 th  Semester
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FILTRATION ,[object Object],[object Object],[object Object],[object Object],[object Object]
 
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Slow Sand Filtration
Removal Of The Vital Layer
Clean Slow Sad Filter Without Water
Mechanism of action of  Slow Sand Filter:   1 .Sedimentation :   The supernatant water acts as a settling reservoir. Settleable particles sink to the sand surface.  2. Mechanical straining :   Particles too big to pass through the interstices between the sand grains are retained.  3 . Adhesion:   The suspended particles that come in contact with the surface of the sand grains are retained by  adhesion to the biological layer (Schmutzdecke) 4. Biochemical processes in the biological layer:  Removes  organic matter, holds back bacteria and oxidizes ammoniacal nitrogen in to nitrates Conversion of soluble iron and manganese compounds into insoluble hydroxides which attach themselves to the sand surfaces
Advantages of slow sand filter ,[object Object],[object Object],[object Object],[object Object]
[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
RIVER In Mixing Chamber: Coagulation by Alum (5-40 mg/litre) Violent mixing of alum (minutes) In Flocculation Chamber: Slow stirring of water by paddles(30 minutes) at 2-4 rpm. Flocculent ppt. of Aluminium Hydroxide entangles all particulate, suspended matter along with bacteria In Sedimentation Chamber: Flocculent ppt. settle down (removal is done time to time) Clear water above goes for filtration Rapid Sand Filter: Remaining alum floc layer over sand bed. it holds back bacteria,  oxidize organic matter Back washing-by air bubbles or water when floc layer becomes very  thick
MIXING CHAMBER FLOCCULATION CHAMBER SEDIMENTATION TANK FILTERS CLEAR WATER STORAGE CONSUMPTION +ALUM COAGULATION PADDLES 30MIN 2-6hrs CHLORINATION
Paddles in a flocculation chamber
Properties Rapid sand filter Slow sand filter Area Small area Large area Rate of filtration(L/m2/hr) 4000-7500 100-400 Sand size (diameter) 0.4-0.7 mm 0.2-0.3 mm Pretreatment Coagulation and sedimentation Sedimentation Filter cleaning Backwashing Scraping Operation More skilled Less skilled Removal of colour Good Better Removal of bacteria 98-99% 99.9%-99.99% Prior water storage Storage needed No need
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[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
PRINCIPLES OF CHLORINATION 1.  Water should be clear, free from turbidity  2.   Chlorine demand  :   Chlorine needed to destroy bacteria, to oxidize organic matter    and to neutralize the ammonia in water 3.Free residual chlorine  for a contact period of 1 hour is essential 4. Breakpoint  :  P oint when chlorine demand of water is met  and  free residual chlorine appears 5 .  Breakpoint chlorination:  Chlorination beyond the breakpoint . The principle of break point chlorination is to add sufficient chlorine  so that 0.5 mg/L  free residual chlorine is present in the water after  one hour of contact time 4. Dose of Chlorine  = Chlorine demand + Free residual chlorine
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[object Object],[object Object],[object Object],[object Object]
[object Object],[object Object],[object Object],[object Object]
[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],Chloramine   ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],0.2-1.5mg/litre 120mm thick film to  Quartz-mercury arc lamps Emitting 200-295nm radiation
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Find volume of water in well (V in Liters) =  3.14 x h x d 2   x 1000 4 Find the amount of bleaching powder needed by Horrock’s apparatus Bleaching powder (max.100 g) mixed with water in a bucket  Allow 10 minutes sedimentation Transfer supernatant chlorine solution to another bucket Deliver chlorine solution in to the well Allow 1 hour contact Do OTA test to measure free residual chlorine If free residual chlorine < 0.5 mg/L  Add more bleaching powder
Inner pot  (28 cm ht) Hole (1 cm dia) Polyethylene foil Hole of 1cm dia Bleaching powder 1kg + 2 kg coarse sand Moist mixture Outer pot (30X25 cm) Rope
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WATER PUTIFICATION METHODS by RAM NAIK

  • 1. RAM NAIK. M 4 th Semester
  • 2.
  • 3.  
  • 4.
  • 5.
  • 6.
  • 7.  
  • 8.
  • 9.
  • 10.
  • 12. Removal Of The Vital Layer
  • 13. Clean Slow Sad Filter Without Water
  • 14. Mechanism of action of Slow Sand Filter: 1 .Sedimentation : The supernatant water acts as a settling reservoir. Settleable particles sink to the sand surface. 2. Mechanical straining : Particles too big to pass through the interstices between the sand grains are retained. 3 . Adhesion: The suspended particles that come in contact with the surface of the sand grains are retained by adhesion to the biological layer (Schmutzdecke) 4. Biochemical processes in the biological layer: Removes organic matter, holds back bacteria and oxidizes ammoniacal nitrogen in to nitrates Conversion of soluble iron and manganese compounds into insoluble hydroxides which attach themselves to the sand surfaces
  • 15.
  • 16.
  • 17. RIVER In Mixing Chamber: Coagulation by Alum (5-40 mg/litre) Violent mixing of alum (minutes) In Flocculation Chamber: Slow stirring of water by paddles(30 minutes) at 2-4 rpm. Flocculent ppt. of Aluminium Hydroxide entangles all particulate, suspended matter along with bacteria In Sedimentation Chamber: Flocculent ppt. settle down (removal is done time to time) Clear water above goes for filtration Rapid Sand Filter: Remaining alum floc layer over sand bed. it holds back bacteria, oxidize organic matter Back washing-by air bubbles or water when floc layer becomes very thick
  • 18. MIXING CHAMBER FLOCCULATION CHAMBER SEDIMENTATION TANK FILTERS CLEAR WATER STORAGE CONSUMPTION +ALUM COAGULATION PADDLES 30MIN 2-6hrs CHLORINATION
  • 19. Paddles in a flocculation chamber
  • 20. Properties Rapid sand filter Slow sand filter Area Small area Large area Rate of filtration(L/m2/hr) 4000-7500 100-400 Sand size (diameter) 0.4-0.7 mm 0.2-0.3 mm Pretreatment Coagulation and sedimentation Sedimentation Filter cleaning Backwashing Scraping Operation More skilled Less skilled Removal of colour Good Better Removal of bacteria 98-99% 99.9%-99.99% Prior water storage Storage needed No need
  • 21.
  • 22.
  • 23. PRINCIPLES OF CHLORINATION 1. Water should be clear, free from turbidity 2. Chlorine demand : Chlorine needed to destroy bacteria, to oxidize organic matter and to neutralize the ammonia in water 3.Free residual chlorine for a contact period of 1 hour is essential 4. Breakpoint : P oint when chlorine demand of water is met and free residual chlorine appears 5 . Breakpoint chlorination: Chlorination beyond the breakpoint . The principle of break point chlorination is to add sufficient chlorine so that 0.5 mg/L free residual chlorine is present in the water after one hour of contact time 4. Dose of Chlorine = Chlorine demand + Free residual chlorine
  • 24.
  • 25.
  • 26.
  • 27.
  • 28.
  • 29.  
  • 30.
  • 31.
  • 32.
  • 33.
  • 34.
  • 35.
  • 36.
  • 37.  
  • 38. Find volume of water in well (V in Liters) = 3.14 x h x d 2 x 1000 4 Find the amount of bleaching powder needed by Horrock’s apparatus Bleaching powder (max.100 g) mixed with water in a bucket Allow 10 minutes sedimentation Transfer supernatant chlorine solution to another bucket Deliver chlorine solution in to the well Allow 1 hour contact Do OTA test to measure free residual chlorine If free residual chlorine < 0.5 mg/L Add more bleaching powder
  • 39. Inner pot (28 cm ht) Hole (1 cm dia) Polyethylene foil Hole of 1cm dia Bleaching powder 1kg + 2 kg coarse sand Moist mixture Outer pot (30X25 cm) Rope
  • 40.
  • 41.