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Lecture on Purification of
          Water by



   Dr. Fazal Mahmood
M.B.B.S(Pb), M.C.P.S(Pak)
Purification on Large scale
 When    sources of water are
  Rivers,Streams,Lakes etc. then water is
  Purified by
 Storage
 Sedimentation
 Filtration(rapid sand & slow sand)
 Disinfection(chlorination)
Purification on Medium Scale
 When   sources of water are
  wells,Springs,Tanks etc.Then water is
  purified by the addition of
 Bleaching powder/Chlorinated Lime as it is
 Cheep
 Easy to use
 Reliable and safe
Purification on Small
    Scale(Domestic Methods)
 BOILING: for 5-10 minutes kills almost
  all organisms & removes temporary
  Hardness.
 DISTILLATION: not commonly used due
  to higher cost, used in Labs. etc.
 ADDITION OF CHEMICALS
 Bleaching Powder: 5% solution is used
  Dose: 3-6 drops/L contact time of ½ hour.
Contnd.-----------
 Chlorine Tablets/Halazone Tablets. one
  tablet/litre.
 Iodine Solution: 02 drops of 2% Soln./litre
 KMnO4: an amount that gives just pink
  coloration to the Water.
 Alum: used for turbid water in a dose of
  0.1-0.4 grains/5 litres of Water.
Purification of water in
      Emergency/Epidemic
 Boiling: for 5-10 minutes.
 High Test Hypo chlorite: used in granular
  form Dose: 01gm./10 litres of water.
 Liquid Bleach/5% Sodium Hypo chlorite
  solution: Dose: 14 ml./1000 litres of water.
 Bleaching Powder: used in a dose of
  2.3gm./1000 litres of water.
Purification of water on Large
             Scale
 On   large scale purification, water is
  disinfected by addition of Chlorine after
  filtration.
 On large scale, water is purified through the
  following processes.
Contnd.---------
A.STORAGE:
 Not a sole measure of purification but
  valuable as a preliminary to other
  processes.
 There is fall in ammonia & rise in nitrates
  due to oxidation of organic matter by
  aerobic bacteria.
Contnd.----------
 Sedimentation,  may be hastened by the
  addition of Alum in a dose of 35 mg./ litre
  for a detention period of 4-6 hrs.
 Sedimentation will prevent clogging of the
  filters.
 Limitation to storage includes algae growth
  which can be controlled by addition of
  CuSo4 in a dose of 1-5 Kg. / 5000 cu.m.
Contnd.---------
B. FILTRATION:
 Filtration through sand is the oldest and
  universally, most accepted method through
  out the world.
 98-99% bacteria are removed along with
  other impurities through filtration.
Types of Filters

 Slow   sand/Biological filters.

 Rapid   sand filters/Mechanical filters.
Slow Sand Filtration
 Firstused in 1804 in Scotland &
  subsequently in London.
 During 19th.Century used through out the
  world.
 Slow sand filter consists of concrete/brick
  work rectangular basin containing carefully
  selected graded sand supported on gravel
  and stones.
Contnd.-----------
    ELEMENTS:
1.   Supernatant (raw) water:
    Upper most layer of raw water(1-1.5M)
    It provides a constant head of water
    It provides a waiting period of 3-12 hours
Elements contnd.-----
2.   Sand Bed:
    It is 1 M thick supported by a layer of fine and
     then coarse gravel and finally by the stones.
3.   Drainage System for filtered water:
    It consists of perforated pipes
4.   Filter Control Valves:
    Valves & Devices incorporated in the outlet-
     pipe system to maintain a constant rate of
     filtration
    Venturi meter measures bed resistance or loss of
     head.
Actions of slow sand filter
 Physical:
  Mechanical straining/sedimentation
 Chemical: Oxidation of organic matter by
  aerobic bacteria.
 Biological: Occurs through “Vital layer”
 Efficiency of the filter depends upon the
  “Vital layer”
Vital Layer
 Slimy   growth known as “Schmutzdecke”,
  Vital layer, zoogleal layer or biological
  layer
 The layer is slimy & gelatinous,It consists
  of threadlike algae & numerous forms of
  life plankton, diatoms and bacteria
 Ripening of the filter
 Vital layer is the “heart” of slow sand filter
ADVANTAGES
 Simple  to construct and operate
 Cost of construction cheaper than rapid
  sand filter
 Process: physical, chemical and biological
 Bacterial count reduction is 99.9% to
  99.99% and E.coli reduction is 99% to
  99.9%
DISADVANTAGES
 Old  fashioned and outdated method of
  water purification (but still in use)
 Initial cost is low but maintenance cost is
  much more than rapid sand filter
 These filters need a lot of space
RAPID SAND FILTERS
 In 1885, first rapid sand filters were
  installed in USA, since that time they are
  gaining considerable popularity in highly
  industrialized countries as well as
  developing world.
Contnd.---------
 TYPES:


1. Open / Gravity type (Peterson’s Filters)

2. Closed / Pressure type (Candy’s Filters)
Contnd.----------
 STEPS   / PROCESSES IN RAPID SAND
  FILTERS
1. COAGULATION:
 Raw water is first treated with Alum in a
  dose of 5-40 mgs./L
 pH has to be adjusted by addition of lime or
  soda ash as Alum needs CaCo3 to form the
  flock.
Contnd.---------
2. RAPID MIXING:
 Water is mixed rapidly with Alum for a
  few minutes in mixing chamber.
3. FLOCCULATION:
 From mixing chamber water is moved into
  the Flocculation chamber where it rests for
  half an hour.
Contd.--------
4. SEDIMENTATION:
 The coagulated water is now led into the
  sedimentation tank where it is detained for
  2-6 hours.
 Flocculant precipitate together with
  impurities & bacteria settle down in the
  tank
Contnd.--------
5. FILTRATION
 Partially clarified water is now subjected to
  the rapid sand filtration.
 Depth of the sand bed is 1 M & each rapid
  sand filter unit has a surface of about 80-90
  Sq.M.
 Oxidation of NH3 also takes place in these
  filters.
ADVANTAGES
 Rapid  sand filters deal with raw water
 directly
 Occupies less space
 Filtration is rapid about 40-50 times as
 compared to slow sand filters
 Washing of filter is easy
 More flexibility in operation
DISADVANTAGES
 Preliminary treatment with Alum is
 required
 Operation is highly skilled
 Removal of color material is less than slow
 sand filter
 Reduction of bacterial count is less than
 slow sand filter
Comparison of Rapid and Slow
             sand filters
                         Rapid.S.F.
      Slow.S.F.
1.    Space:               Occupies little space-----Occupies large area
2.    Rate of filtration:    5-15 cu.m./sq.m./hr.----- 0.1-0.4
3.    Effective sand size:   0.4-0.7mm-----------------0.2-0.3mm
4.    Preliminary treatment: Coagulation& sedimentation--plain
      Sediment
5.    Washing:               By back washing--------By scraping the sand
6.    Loss of head allowed: 6-8 feet--------------------4feet
7.    Removal of turbidity: Good-----------------------Good
8.    Removal of color:       Good------------------------Fair
9.    Removal of bacteria: 98-99 %--------------------99.9-99.99
DISINFECTION OF WATER
  CHEMICAL METHODS / GERMICIDES
1. CHLORINE: is used for purification of water on large
   scale
2. KMnO4: used for disinfection of water in wells especially
   during epidemics
3. CuSO4/CaCl2: used for the removal of algae
4. Lime: used for muddy water
5. Ozonization & U.V. irradiation: both methods are used for
   disinfection of water in swimming pools
6. Katadyn Silver: sand coated with silver used in slow sand
   filters instead of plain sand
7. Charcoal: used as adsorbent to remove color,odor & taste
Disinfection of Wells
    The most effective & cheapest method of
     disinfecting wells is by bleaching powder
    STEPS IN WELL DISINFECTION :
1.   Find the volume of water in a well:
a.   Measure the depth of water column..(h) M
b.   Measure the diameter of well………(d) M
c.   Substitute h and d in:
Cotnd…….
                   3.14 x (d)2 x h
Volume(litres)=------------------------------ x 100
                           4
d.   One cubic meter = 1,000 litres of water

     Find the amount of bleaching powder
     required for disinfection:

     Estimate the Chlorine demand of well
     water by HORROCK’S APPARATUS
Contnd……..
3. Dissolve Bleaching Powder in water

4. Delivery of Chlorine solution into the well

5. Contact period

6. Orthotolidine arsenite test
Chlorination of water
 It is the most widely used method for water
  purification, both on large as well as on
  small scale.
 It is the most reliable and cheapest method.
 It is supplement but not the substitute to
  sand filtration.
Properties of Chlorine
 Killing of pathogenic bacteria by inhibiting their
  protein synthesis.
 Oxidizes Iron, Manganese & Hydrogen Sulphide.
 Destroys taste & odor producing constituents.
 It controls algae growth.
 It helps in coagulation and suspension of the
  organic matter.
Action Of Chlorine
 When   chlorine is added to water it forms
  HCl & HOCl.
 The disinfecting action of chlorine is mainly
  due to Hypochlrous acid & to a small extent
  due to Hypochlorite Ions.
 Hypochorous acid is 70-80 times more
  effective than Hypochlorite Ions.
Actions of Chlorine depends
           upon the……..
 Organic matter
 Metals
 Bacterial content
 Temperature & pH of water.
 Suspended matter and,
 Amount of free residual chlorine in water
Contnd………
 Efficiency
           of chlorine increases, when it
  combines with Ammonia and……

 Itdecreases, when it combines with
  Sulphides, Ferrous salts & inert matter in
  suspension form
Principles of Chlorination
 Water   to be chlorinated must be free from
  turbidity
 Chlorine demand of water should be
  estimated
 Contact period of one hour is essential to
  kill the bacteria and viruses
 Minimum recommended concentration for
  free chlorine is 0.5mg. / liter
Chlorine demand of water
 Is  the difference between the amount of
  chlorine added to water and the amount of
  residual chlorine remaining at the end of a
  specific period of contact (usually 60 min.)
  at a given temperature and pH of water.
 ACUAL DOSE OF CHLORINE:
  It is the sum of chlorine demand of water
  and free residual chlorine
Methods of Chlorination
1.   Chlorine gas
2.   Chloramine
3.   Perchloron (H.T.H.)
     TYPES OF CHLORINATION:
a.   Superchlorination
b.   Break Point Chlorination
Tests for the presence of
       Chlorine in Water
   Orthotolidine (O.T.) Test

   Orthotolidine-Arsenite (O.T.A.) Test

   Starch Iodide Test
Surveillance of drinking Water
1.   Sanitary survey
2.   Sampling
3.   Bacteriological surveillance
4.   Biological examination
5.   Chemical surveillance
Sampling of Water
    Collection, Storage & Transportation of water
     samples from……
    Taps
    Rivers
    Streams
    Tanks
    Wells
A.   For Physical & Chemical Examination
B.   For Bacteriological Examination
    PERTICULARS OF A SAMPLE
Standards of Water
 PHYSICAL    STANDARDS
 Turbidity
 Color
 Odor
 Taste
Contnd………
 CHEMICAL     STANDARDS
   Hardness
   Chlorides
   Ammonia
   Nitrites
   Nitrates
   Absorbed Oxygen
   Dissolved Oxygen
Contnd……..
 Toxic substances and a specific group of
  chemicals causing Non-Specific diseases of
  water
 Poly-nuclear Aromatic Hydrocarbons and
  Radioactive substances ( a group of
  chemical substances of water affecting the
  acceptability of water.
Bacteriological Standards
1.BACTERIAL STANDARDS :
  W.H.O. recommended these standards in
  1984 for Public water supplies
 Ideally all samples taken from the
  distribution system should be free from
  Coliform organisms
 In Practice this standard is not always
  attainable
Recommended Standards for
  Water samples collected
 Throughout  any year 95 % samples 100 ml.
  each should not contain any Coliform
  organisms
 No samples should contain E.coli
 No sample should contain more than 03
  Coliform
 Any two consecutive samples should not
  contain Coliform
Contnd………
 Incase of Individual / Small water
  supplies such as from household Tap, Well,
  Spring etc.
 Coliform count should not exceed 10 /100
  ml. and E.coli should be nil
Contnd………..
2. VIRAL STANDARDS :
 W.H.O. Standards fix the limit for viruses
  such as Eneroviruses, Retroviruses &
  Adenoviruses in water supplies at 01 Plaque
  forming unit
 Faecal Bacteroiphage & Enteropathogenic
  viruses should be completely absent
Bacteriological Indicators
     These are based on organisms indicative of
     faecal pollution, These organisms include!

1. E.coli and Coliform group as a whole
2. Faecal Streptococci
3. Clostridium Perfringens
4. Examination for Protozoa, Parasitic
   worms & Larvae is also recommended
Contnd……..
    Reasons why Coliform organisms are chosen
     as indicators of Faecal Pollution
1.   Constantly present in human intestine an
     average person excretes 200-400 billions / day
     of these organisms in faeces
2.   They are foreign to potable water supplies
3.   Easily detectable by ordinary cultural methods
4.   Survival time is much better than other
     organisms
5.   Have greater resistance to natural forces of
     purification
Contnd……..
 FAECAL    STREPTOCOCCI :

 Faecal Strepococci occur regularly in much
  smaller number than E.coli
 Their presence is regarded as confirmatory
  evidence of recent faecal contamination of
  water in doubtful cases
Contnd………
 CLOSTRIDIUM       PERFRINGENS :

 They  are spore bearing organisms
 Their presence along with Coliform indicate
  recent water contamination
 While the presence of their spores but the
  absence of Coliform confirms remote
  contamination of water

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Lecture on purification of water by

  • 1. Lecture on Purification of Water by Dr. Fazal Mahmood M.B.B.S(Pb), M.C.P.S(Pak)
  • 2. Purification on Large scale  When sources of water are Rivers,Streams,Lakes etc. then water is Purified by  Storage  Sedimentation  Filtration(rapid sand & slow sand)  Disinfection(chlorination)
  • 3. Purification on Medium Scale  When sources of water are wells,Springs,Tanks etc.Then water is purified by the addition of  Bleaching powder/Chlorinated Lime as it is  Cheep  Easy to use  Reliable and safe
  • 4. Purification on Small Scale(Domestic Methods)  BOILING: for 5-10 minutes kills almost all organisms & removes temporary Hardness.  DISTILLATION: not commonly used due to higher cost, used in Labs. etc.  ADDITION OF CHEMICALS  Bleaching Powder: 5% solution is used Dose: 3-6 drops/L contact time of ½ hour.
  • 5. Contnd.-----------  Chlorine Tablets/Halazone Tablets. one tablet/litre.  Iodine Solution: 02 drops of 2% Soln./litre  KMnO4: an amount that gives just pink coloration to the Water.  Alum: used for turbid water in a dose of 0.1-0.4 grains/5 litres of Water.
  • 6. Purification of water in Emergency/Epidemic  Boiling: for 5-10 minutes.  High Test Hypo chlorite: used in granular form Dose: 01gm./10 litres of water.  Liquid Bleach/5% Sodium Hypo chlorite solution: Dose: 14 ml./1000 litres of water.  Bleaching Powder: used in a dose of 2.3gm./1000 litres of water.
  • 7. Purification of water on Large Scale  On large scale purification, water is disinfected by addition of Chlorine after filtration.  On large scale, water is purified through the following processes.
  • 8. Contnd.--------- A.STORAGE:  Not a sole measure of purification but valuable as a preliminary to other processes.  There is fall in ammonia & rise in nitrates due to oxidation of organic matter by aerobic bacteria.
  • 9. Contnd.----------  Sedimentation, may be hastened by the addition of Alum in a dose of 35 mg./ litre for a detention period of 4-6 hrs.  Sedimentation will prevent clogging of the filters.  Limitation to storage includes algae growth which can be controlled by addition of CuSo4 in a dose of 1-5 Kg. / 5000 cu.m.
  • 10. Contnd.--------- B. FILTRATION:  Filtration through sand is the oldest and universally, most accepted method through out the world.  98-99% bacteria are removed along with other impurities through filtration.
  • 11. Types of Filters  Slow sand/Biological filters.  Rapid sand filters/Mechanical filters.
  • 12. Slow Sand Filtration  Firstused in 1804 in Scotland & subsequently in London.  During 19th.Century used through out the world.  Slow sand filter consists of concrete/brick work rectangular basin containing carefully selected graded sand supported on gravel and stones.
  • 13. Contnd.-----------  ELEMENTS: 1. Supernatant (raw) water:  Upper most layer of raw water(1-1.5M)  It provides a constant head of water  It provides a waiting period of 3-12 hours
  • 14. Elements contnd.----- 2. Sand Bed:  It is 1 M thick supported by a layer of fine and then coarse gravel and finally by the stones. 3. Drainage System for filtered water:  It consists of perforated pipes 4. Filter Control Valves:  Valves & Devices incorporated in the outlet- pipe system to maintain a constant rate of filtration  Venturi meter measures bed resistance or loss of head.
  • 15. Actions of slow sand filter  Physical: Mechanical straining/sedimentation  Chemical: Oxidation of organic matter by aerobic bacteria.  Biological: Occurs through “Vital layer”  Efficiency of the filter depends upon the “Vital layer”
  • 16. Vital Layer  Slimy growth known as “Schmutzdecke”, Vital layer, zoogleal layer or biological layer  The layer is slimy & gelatinous,It consists of threadlike algae & numerous forms of life plankton, diatoms and bacteria  Ripening of the filter  Vital layer is the “heart” of slow sand filter
  • 17. ADVANTAGES  Simple to construct and operate  Cost of construction cheaper than rapid sand filter  Process: physical, chemical and biological  Bacterial count reduction is 99.9% to 99.99% and E.coli reduction is 99% to 99.9%
  • 18. DISADVANTAGES  Old fashioned and outdated method of water purification (but still in use)  Initial cost is low but maintenance cost is much more than rapid sand filter  These filters need a lot of space
  • 19. RAPID SAND FILTERS  In 1885, first rapid sand filters were installed in USA, since that time they are gaining considerable popularity in highly industrialized countries as well as developing world.
  • 20. Contnd.---------  TYPES: 1. Open / Gravity type (Peterson’s Filters) 2. Closed / Pressure type (Candy’s Filters)
  • 21. Contnd.----------  STEPS / PROCESSES IN RAPID SAND FILTERS 1. COAGULATION:  Raw water is first treated with Alum in a dose of 5-40 mgs./L  pH has to be adjusted by addition of lime or soda ash as Alum needs CaCo3 to form the flock.
  • 22. Contnd.--------- 2. RAPID MIXING:  Water is mixed rapidly with Alum for a few minutes in mixing chamber. 3. FLOCCULATION:  From mixing chamber water is moved into the Flocculation chamber where it rests for half an hour.
  • 23. Contd.-------- 4. SEDIMENTATION:  The coagulated water is now led into the sedimentation tank where it is detained for 2-6 hours.  Flocculant precipitate together with impurities & bacteria settle down in the tank
  • 24. Contnd.-------- 5. FILTRATION  Partially clarified water is now subjected to the rapid sand filtration.  Depth of the sand bed is 1 M & each rapid sand filter unit has a surface of about 80-90 Sq.M.  Oxidation of NH3 also takes place in these filters.
  • 25. ADVANTAGES  Rapid sand filters deal with raw water directly  Occupies less space  Filtration is rapid about 40-50 times as compared to slow sand filters  Washing of filter is easy  More flexibility in operation
  • 26. DISADVANTAGES  Preliminary treatment with Alum is required  Operation is highly skilled  Removal of color material is less than slow sand filter  Reduction of bacterial count is less than slow sand filter
  • 27. Comparison of Rapid and Slow sand filters Rapid.S.F. Slow.S.F. 1. Space: Occupies little space-----Occupies large area 2. Rate of filtration: 5-15 cu.m./sq.m./hr.----- 0.1-0.4 3. Effective sand size: 0.4-0.7mm-----------------0.2-0.3mm 4. Preliminary treatment: Coagulation& sedimentation--plain Sediment 5. Washing: By back washing--------By scraping the sand 6. Loss of head allowed: 6-8 feet--------------------4feet 7. Removal of turbidity: Good-----------------------Good 8. Removal of color: Good------------------------Fair 9. Removal of bacteria: 98-99 %--------------------99.9-99.99
  • 28. DISINFECTION OF WATER  CHEMICAL METHODS / GERMICIDES 1. CHLORINE: is used for purification of water on large scale 2. KMnO4: used for disinfection of water in wells especially during epidemics 3. CuSO4/CaCl2: used for the removal of algae 4. Lime: used for muddy water 5. Ozonization & U.V. irradiation: both methods are used for disinfection of water in swimming pools 6. Katadyn Silver: sand coated with silver used in slow sand filters instead of plain sand 7. Charcoal: used as adsorbent to remove color,odor & taste
  • 29. Disinfection of Wells  The most effective & cheapest method of disinfecting wells is by bleaching powder  STEPS IN WELL DISINFECTION : 1. Find the volume of water in a well: a. Measure the depth of water column..(h) M b. Measure the diameter of well………(d) M c. Substitute h and d in:
  • 30. Cotnd……. 3.14 x (d)2 x h Volume(litres)=------------------------------ x 100 4 d. One cubic meter = 1,000 litres of water Find the amount of bleaching powder required for disinfection: Estimate the Chlorine demand of well water by HORROCK’S APPARATUS
  • 31. Contnd…….. 3. Dissolve Bleaching Powder in water 4. Delivery of Chlorine solution into the well 5. Contact period 6. Orthotolidine arsenite test
  • 32. Chlorination of water  It is the most widely used method for water purification, both on large as well as on small scale.  It is the most reliable and cheapest method.  It is supplement but not the substitute to sand filtration.
  • 33. Properties of Chlorine  Killing of pathogenic bacteria by inhibiting their protein synthesis.  Oxidizes Iron, Manganese & Hydrogen Sulphide.  Destroys taste & odor producing constituents.  It controls algae growth.  It helps in coagulation and suspension of the organic matter.
  • 34. Action Of Chlorine  When chlorine is added to water it forms HCl & HOCl.  The disinfecting action of chlorine is mainly due to Hypochlrous acid & to a small extent due to Hypochlorite Ions.  Hypochorous acid is 70-80 times more effective than Hypochlorite Ions.
  • 35. Actions of Chlorine depends upon the……..  Organic matter  Metals  Bacterial content  Temperature & pH of water.  Suspended matter and,  Amount of free residual chlorine in water
  • 36. Contnd………  Efficiency of chlorine increases, when it combines with Ammonia and……  Itdecreases, when it combines with Sulphides, Ferrous salts & inert matter in suspension form
  • 37. Principles of Chlorination  Water to be chlorinated must be free from turbidity  Chlorine demand of water should be estimated  Contact period of one hour is essential to kill the bacteria and viruses  Minimum recommended concentration for free chlorine is 0.5mg. / liter
  • 38. Chlorine demand of water  Is the difference between the amount of chlorine added to water and the amount of residual chlorine remaining at the end of a specific period of contact (usually 60 min.) at a given temperature and pH of water.  ACUAL DOSE OF CHLORINE: It is the sum of chlorine demand of water and free residual chlorine
  • 39. Methods of Chlorination 1. Chlorine gas 2. Chloramine 3. Perchloron (H.T.H.) TYPES OF CHLORINATION: a. Superchlorination b. Break Point Chlorination
  • 40. Tests for the presence of Chlorine in Water  Orthotolidine (O.T.) Test  Orthotolidine-Arsenite (O.T.A.) Test  Starch Iodide Test
  • 41. Surveillance of drinking Water 1. Sanitary survey 2. Sampling 3. Bacteriological surveillance 4. Biological examination 5. Chemical surveillance
  • 42. Sampling of Water  Collection, Storage & Transportation of water samples from……  Taps  Rivers  Streams  Tanks  Wells A. For Physical & Chemical Examination B. For Bacteriological Examination  PERTICULARS OF A SAMPLE
  • 43. Standards of Water  PHYSICAL STANDARDS  Turbidity  Color  Odor  Taste
  • 44. Contnd………  CHEMICAL STANDARDS  Hardness  Chlorides  Ammonia  Nitrites  Nitrates  Absorbed Oxygen  Dissolved Oxygen
  • 45. Contnd……..  Toxic substances and a specific group of chemicals causing Non-Specific diseases of water  Poly-nuclear Aromatic Hydrocarbons and Radioactive substances ( a group of chemical substances of water affecting the acceptability of water.
  • 46. Bacteriological Standards 1.BACTERIAL STANDARDS : W.H.O. recommended these standards in 1984 for Public water supplies  Ideally all samples taken from the distribution system should be free from Coliform organisms  In Practice this standard is not always attainable
  • 47. Recommended Standards for Water samples collected  Throughout any year 95 % samples 100 ml. each should not contain any Coliform organisms  No samples should contain E.coli  No sample should contain more than 03 Coliform  Any two consecutive samples should not contain Coliform
  • 48. Contnd………  Incase of Individual / Small water supplies such as from household Tap, Well, Spring etc.  Coliform count should not exceed 10 /100 ml. and E.coli should be nil
  • 49. Contnd……….. 2. VIRAL STANDARDS :  W.H.O. Standards fix the limit for viruses such as Eneroviruses, Retroviruses & Adenoviruses in water supplies at 01 Plaque forming unit  Faecal Bacteroiphage & Enteropathogenic viruses should be completely absent
  • 50. Bacteriological Indicators These are based on organisms indicative of faecal pollution, These organisms include! 1. E.coli and Coliform group as a whole 2. Faecal Streptococci 3. Clostridium Perfringens 4. Examination for Protozoa, Parasitic worms & Larvae is also recommended
  • 51. Contnd……..  Reasons why Coliform organisms are chosen as indicators of Faecal Pollution 1. Constantly present in human intestine an average person excretes 200-400 billions / day of these organisms in faeces 2. They are foreign to potable water supplies 3. Easily detectable by ordinary cultural methods 4. Survival time is much better than other organisms 5. Have greater resistance to natural forces of purification
  • 52. Contnd……..  FAECAL STREPTOCOCCI :  Faecal Strepococci occur regularly in much smaller number than E.coli  Their presence is regarded as confirmatory evidence of recent faecal contamination of water in doubtful cases
  • 53. Contnd………  CLOSTRIDIUM PERFRINGENS :  They are spore bearing organisms  Their presence along with Coliform indicate recent water contamination  While the presence of their spores but the absence of Coliform confirms remote contamination of water