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Water purification
p.bonehoeffer
• Water purification is the process of removing
undesirable chemicals, biological
contaminants, suspended solids and gases from
water.
• The goal is to produce water for a specific
purpose
Main steps of water purification
• Coagulation and flocculation
• Sedimentation
• Filtration
• Aeration
• Chemical treatment
• Disinfection
Coagulation and flocculation
• Coagulation and flocculation are used to remove
color, turbidity, algae and other microorganisms from
surface waters.
• The addition of a chemical coagulant to the water
causes the formation of a precipitate, or floc, which
entraps these impurities. Iron and aluminium can also
be removed under suitable conditions.
• The floc is separated from the treated water by
sedimentation and/or filtration, although flotation
processes may be used in place of sedimentation.
• The most commonly used coagulants are aluminium
sulphate and ferric sulphate.
• Coagulants are dosed in solution at a rate determined
by raw water quality near the inlet of a mixing tank or
flocculator.
• The advantages of coagulation are that it reduces the
time required to settle out suspended solids and is
very effective in removing fine particles that are
otherwise very difficult to remove. Coagulation can
also be effective in removing many protozoa, bacteria
and viruses.
Sedimentation
• Simple sedimentation may be used to reduce turbidity
and solids in suspension.
• Sedimentation tanks are designed to reduce the
velocity of flow of water so as to permit suspended
solids to settle under gravity.
Filtration
Filters can also remove smaller particles like silt and
suspended solids; dissolved ions and some filters catch
bacteria and viruses.
• There are many types of filtration method such as
i. screens,
ii. gravel filters,
iii. slow sand,
iv. rapid sand filters or cartridge filters.
 slow sand and rapid sand filters are mainly used
• Rapid sand filters filter water through sand, but speed
up the process by using chemicals as well.
• Slow sand filters however, use no chemicals or
electricity to function, but they are often large and
require large areas.
• Slow sand filters consist of a layer of fine grain sand
supported on a layer of gravel, the topmost layer
consisting of a biofilm bacteria fungi and a range of
aquatic larvae that have been caught there.
• Sand filters require some time to mature, usually 10-20
days before the filtered water is safe to drink.
Aeration
• Air stripping is used for removal of volatile
organics (e.g. solvents), carbon dioxide,
disinfection by-products, some taste and odor
causing compounds.
• Aeration processes are designed to achieve
efficient mass transfer of oxygen into water
and removal of gases and volatile compounds
by air stripping. Oxygen transfer can usually be
achieved using a diffusion of air into water,
without the need for elaborate equipment.
Chemical treatment
Control of pH
The pH value of water may need to be adjusted during
treatment and before distribution.
• to ensure that the pH value meets the water quality
standards
• Where necessary, reduction of pH can be achieved by
dosing with a suitable acid such as sulphuric acid,
hydrochloric acid, or carbon dioxide.
• Many raw surface waters are slightly acidic and coagulation
processes further increase acidity. Increase of pH can be
achieved by:
• dosing with sodium hydroxide, calcium hydroxide or
sodium carbonate
• passage of the water through a bed of alkaline
medium
• removal of excess carbon dioxide by aeration
Disinfection
• Contamination by sewage or animal faeces is the
greatest danger associated with water for drinking.
This is because sewage from human or animal
sources may contain the causative organisms of many
communicable diseases.
• The use of disinfection to kill or inactivate pathogenic
microorganisms is necessary if the raw water contains
organisms.
Ex: E. coli
• Several disinfection methods are used in water
treatment.
– Disinfection with chlorine is the most widely used
method for large water supplies but its application
is less common in small supplies.
– Ultraviolet irradiation is the most common
disinfection method found in private supplies.
Disinfection with chlorine
• Chlorine, whether in the form of pure chlorine gas,
sodium hypochlorite or calcium hypochlorite,
dissolves in water to form hypochlorous acid (HOCl)
Cl2 + H2O ⇔ HOCl + HCl
• Hypochlorous acid is a weak acid which undergoes
partial dissociation to produce a hydrogen ion (H+)
and a hypochlorite ion (OCl–):
HOCl ⇔ H+ + OCl–
• The total concentration of chlorine, hypochlorous
acid and hypochlorite ions is referred to as the free
available chlorine.
• If ammonia is present in the raw water, the
hypochlorous acid can react to produce chloramines.
• Combined available chlorine is a less powerful
disinfectant than free available chlorine but gives a
more persistent residual.
• NH3 ⇒ NH2Cl ⇒ NHCl2 ⇒ NHCl3
• The effectiveness of chlorine for disinfection depends
on the form of chlorine, its concentration and the
contact time. Hypochlorous acid is a more powerful
disinfectant than the hypochlorite ion and
chlorination is usually practiced at values of pH
favorable to its formation.
• resulting in a free chlorine residual of 0.2 to 0.5mg/l”.
Water purificatin
Water purificatin

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Water purificatin

  • 2. • Water purification is the process of removing undesirable chemicals, biological contaminants, suspended solids and gases from water. • The goal is to produce water for a specific purpose
  • 3.
  • 4. Main steps of water purification • Coagulation and flocculation • Sedimentation • Filtration • Aeration • Chemical treatment • Disinfection
  • 5. Coagulation and flocculation • Coagulation and flocculation are used to remove color, turbidity, algae and other microorganisms from surface waters. • The addition of a chemical coagulant to the water causes the formation of a precipitate, or floc, which entraps these impurities. Iron and aluminium can also be removed under suitable conditions. • The floc is separated from the treated water by sedimentation and/or filtration, although flotation processes may be used in place of sedimentation.
  • 6. • The most commonly used coagulants are aluminium sulphate and ferric sulphate. • Coagulants are dosed in solution at a rate determined by raw water quality near the inlet of a mixing tank or flocculator. • The advantages of coagulation are that it reduces the time required to settle out suspended solids and is very effective in removing fine particles that are otherwise very difficult to remove. Coagulation can also be effective in removing many protozoa, bacteria and viruses.
  • 7.
  • 8. Sedimentation • Simple sedimentation may be used to reduce turbidity and solids in suspension. • Sedimentation tanks are designed to reduce the velocity of flow of water so as to permit suspended solids to settle under gravity.
  • 9.
  • 10. Filtration Filters can also remove smaller particles like silt and suspended solids; dissolved ions and some filters catch bacteria and viruses. • There are many types of filtration method such as i. screens, ii. gravel filters, iii. slow sand, iv. rapid sand filters or cartridge filters.  slow sand and rapid sand filters are mainly used
  • 11. • Rapid sand filters filter water through sand, but speed up the process by using chemicals as well. • Slow sand filters however, use no chemicals or electricity to function, but they are often large and require large areas. • Slow sand filters consist of a layer of fine grain sand supported on a layer of gravel, the topmost layer consisting of a biofilm bacteria fungi and a range of aquatic larvae that have been caught there. • Sand filters require some time to mature, usually 10-20 days before the filtered water is safe to drink.
  • 12.
  • 13. Aeration • Air stripping is used for removal of volatile organics (e.g. solvents), carbon dioxide, disinfection by-products, some taste and odor causing compounds. • Aeration processes are designed to achieve efficient mass transfer of oxygen into water and removal of gases and volatile compounds by air stripping. Oxygen transfer can usually be achieved using a diffusion of air into water, without the need for elaborate equipment.
  • 14.
  • 15. Chemical treatment Control of pH The pH value of water may need to be adjusted during treatment and before distribution. • to ensure that the pH value meets the water quality standards • Where necessary, reduction of pH can be achieved by dosing with a suitable acid such as sulphuric acid, hydrochloric acid, or carbon dioxide.
  • 16. • Many raw surface waters are slightly acidic and coagulation processes further increase acidity. Increase of pH can be achieved by: • dosing with sodium hydroxide, calcium hydroxide or sodium carbonate • passage of the water through a bed of alkaline medium • removal of excess carbon dioxide by aeration
  • 17. Disinfection • Contamination by sewage or animal faeces is the greatest danger associated with water for drinking. This is because sewage from human or animal sources may contain the causative organisms of many communicable diseases. • The use of disinfection to kill or inactivate pathogenic microorganisms is necessary if the raw water contains organisms. Ex: E. coli
  • 18. • Several disinfection methods are used in water treatment. – Disinfection with chlorine is the most widely used method for large water supplies but its application is less common in small supplies. – Ultraviolet irradiation is the most common disinfection method found in private supplies.
  • 19. Disinfection with chlorine • Chlorine, whether in the form of pure chlorine gas, sodium hypochlorite or calcium hypochlorite, dissolves in water to form hypochlorous acid (HOCl) Cl2 + H2O ⇔ HOCl + HCl • Hypochlorous acid is a weak acid which undergoes partial dissociation to produce a hydrogen ion (H+) and a hypochlorite ion (OCl–): HOCl ⇔ H+ + OCl–
  • 20. • The total concentration of chlorine, hypochlorous acid and hypochlorite ions is referred to as the free available chlorine. • If ammonia is present in the raw water, the hypochlorous acid can react to produce chloramines. • Combined available chlorine is a less powerful disinfectant than free available chlorine but gives a more persistent residual. • NH3 ⇒ NH2Cl ⇒ NHCl2 ⇒ NHCl3
  • 21. • The effectiveness of chlorine for disinfection depends on the form of chlorine, its concentration and the contact time. Hypochlorous acid is a more powerful disinfectant than the hypochlorite ion and chlorination is usually practiced at values of pH favorable to its formation. • resulting in a free chlorine residual of 0.2 to 0.5mg/l”.