SlideShare a Scribd company logo
Disinfection
Biological water quality
• Assessed by MPN test
• Multiple tube fermentation technique
• Membrane filtration technique
• Improvement by physical separation or removal of pathogens
• Filtration (and membrane filtration, UF!), Coagulation-
flocculation, and Settling
• Improvement by disinfection: deactivation (render harmless) of
pathogens (causing water borne diseases)
Disinfection two types
• Primary disinfection: achieving desired level of microbial kills or
inactivation
• Secondary disinfection: maintaining disinfectant residual in finished
water to prevent regrowth of microorganisms
Biological water quality and Disinfection
Disinfectants
• Ideal disinfectants
– Versatile (effective against all types of pathogens), Fast-acting
(effective within short contact times), and Robust (effective in
the presence of interfering materials)
– Easy to handle (non-toxic, non-flammable, non-explosive ,
soluble) and Compatible with various materials/surfaces in
WTPs (pipes, equipments)
– Economical (cheap)
– Toxic to microorganisms well below the toxic thresholds to
humans and higher animals
– Should persist enough to prevent re-growth in the distribution
system
– Should not form the undesirable disinfection byproducts (DBPs)
No disinfectant used is ideal disinfectant
Disinfectants
• Commonly used disinfectants are
– Chemical agents (disinfectants): Chlorine, hypochlorite, Chlorine
dioxide (twin oxide) and Chloramines; Ozone; Peroxide, etc.
– Irradiation (UV radiation) and Heating (to boiling!)
– Sonification, electrocution, etc.
• Different disinfectants are effective at different
concentrations/ doses
• Tolerance levels against a disinfectant are different for
different organisms
– Cysts, encysted bacteria, bacterial spores, etc. could be more
resistant or more tolerant to disinfectant
• Factors such as turbidity offer sanctuary and provide shield
against disinfection
• Disinfectants through reacting with water and its constituents
(metals, ammonia, organics, etc.) can form disinfection
byproducts (DBPs), and cause taste and odour problems
Disinfection kinetics
kt
N
N
kN
dt
dN







0
ln
N is the number of microbes
‘t’ is contact time
‘k’ is disinfection rate constant
Contact time (Chick’s law)
When the disinfectant level is held constant
Equal susceptibility and uniform dispersion of the microbes is assumed
 
21
12
1
2
ln
TRT
TTE
K
K a 






Disinfection is temperature sensitive
Activation energy (Ea)
R is gas constant (8.314 J/mol.K)
Kills double with 10°C temp. raise
Disinfection is function of both time and concentration (C)
tCk
N
N n
0
0
ln Chick-Watson law
Disinfection is pH sensitive
Ozone is more effective at lower pH
Chlorine (OCl-/HOCl) is more effective at lower pH
ClO2 is more effective at higher pH
Disinfection
K0 for 99% kills at 5°C
CT values for inactivation using ClO2
Chlorination – Chemistry
Objectives of chlorination: Disinfection, H2S control, sludge
bulking control, odour control, etc.
Chlorine as gas and sodium/calcium hypochlorite are used
– Large systems use chlorine gas
The chlorine based disinfectants release HOCl or OCl-
pH and temperature determine the equilibrium relationship
– HOCl levels are higher at lower pH (at <5 pH all chlorine is HOCl,
76% HOCl at 7.0 pH, 33% at 7.8 pH and ~0% at >10 pH)
– HOCl fraction increases with decreasing temperature
Sum of HOCl and OCl- is known as free residual chlorine
HOClHOHCl  
22

 OClCaOClCa 2)( 2
2

 OClNaNaOCl

 OClHHOCl
  
 HOCl
OClH
Ka


HOCl is more effective than
OCl- as disinfectant
Cat
CatpKa


082.7
2058.7
Chlorine reacts with reduced materials (Fe2+, Mn2+, H2S, organics, NH3, etc.)
Breakpoint Chlorination
• Chlorine gas is highly oxidizing, toxic, corrosive and hazardous
yellow-green gas (supplied as liquid chlorine in bullets)
• Can be lethal to human beings at 0.1% (volume) concentration
• Heavier than air and spreads slowly at ground level
• Effective against all types of microbes as both primary and
secondary disinfectant
• Leaves combined and free residual chlorine in the treated water
and this can be responsible for secondary disinfection
• Chlorine handling requires specialized equipment, care and skill
• A separate storage room (not connected to other rooms) with
doors opening to outside, and with view windows for inspection
• Chlorinator installed in the rooms with direct emergency access
to outside air
• Self contained breathing apparatus and chlorine cylinder repair
kit must be readily accessible
• Masks, air tanks, chlorine detection devices etc. needed
Disinfection by Chlorine gas
• Liquid chlorine is drawn out, vapourized (supply latent heat!)
and dosed into water by an injector
• Highly pressurized water is passed through a venturi – vacuum
created sucks chlorine gas into the water stream
• Provisions are made for proper mixing of the chlorine dosed and
for the requisite contact time
• pH control may be necessary for effective disinfection (chlorine
gas on dissolution also reduces the pH)
• Alternatively the chlorine gas is dissolved in water to form
chlorine solution and this in turn is dosed/injected into water
– Solubility is 750 mg/l at usual pH and temperature
• Dechlorination of the chlorinated water is often needed for the
removal of the residual chlorine
– SO2, Na2SO3, sodium metabisulfite, activated carbon can be used
Disinfection by Chlorine gas
Chlorine gas application system
Chlorine dose
• Dose range is known from break point chlorination and water flow
rates
– Water characteristics and residual chlorine desired in water influence
the dose
• Feedback control involving residual chlorine monitoring is followed
Injection and initial mixing
• Withdrawn from the bullet as gas and applied either directly or
indirectly as aqueous solution
– Evaporators are used if withdrawal is >180 kg/day
– Evaporators are used for gasification when withdrawal rate is >18
kg/day for 68 kg cylinders and >205 kg/day for 908 kg cylinders
• Black steel piping is used for dry chlorine (liquid or gas) conveyance
and PVC piping (schedule-80) for chlorine solution
• Diffuser (plastic pipe with perforations) is used for chlorine dosing
• Mechanical mixing, static inline mixing or hydrodynamic mixing is
used for the mixing of chlorine with water
Design of chlorination
09 chlorination
Chlorine contact basin (WHO recommends 15 mg-min/L)
• Contact basin is eliminated if travel time of water in the supply
pipeline is greater than the needed chlorine contact time
• Long plug flow chambers (with 20:1 to 40:1 aspect ratio) are
used
• Compacted into rectangular tanks with baffles
• Hydraulic dead zones and hydraulic short-circuiting are
associated with the chlorine contact basins
– Submerged baffles, guide vanes and rounded corners are used to
avoid the problems
Design of chlorination
Corrections to C-t
Temp. and pH correction
Df of contact tank
MPN number
6-10% of the total cross-sectional area is
openings in the submerged baffles
09 chlorination
• A separate storage room (not connected to other rooms) with
doors opening to outside
• Ventilation at floor level to storage chamber with capacity of
60 air changes per hour
• Fixed glass viewing window for checking leaks prior to entry
• Fan controls at the room entrance
• Protect storage and feed facilities from fire hazards
• Provide leak detection equipment connected to alarm system
• Protect cylinders from direct sun light during summer warm
climates
• Spill control and containment and emergency caustic
scrubbing system to neutralize leaks
– Containment vessels to provide total enclosure of cylinder
– In the event of cylinder failure gas is contained within and
processed at normal rate through chlorination facilities
Chlorine storage facilities
• More expensive than Cl2 and highly corrosive
• Available as a solution with 5-15% available chlorine level
• Decomposes on storage
– Should not be stored beyond a month and should be stored in
cool, dark and dry areas
• Easier to handle than calcium hypochlorite and chlorine gas
• Preferred for highly populated areas and small scale applications
• The sodium hypochlorinator includes a solution tank, dosing
pumps, tubing and diffuser
– The solution is injected into water supply pipe at controlled rate
• On dissolution sodium hypochlorite forms OCl- (less effective as
disinfectant than HOCl)
• Sodium hypochlorite can be generated onsite by electrolysis of
sodium chloride solution (electro-chlorinators!)
– Hydrogen is given off here as a byproduct

 OClNaNaOCl
Disinfection by sodium hypochlorite
• A white solid soluble in water and has about 65% available
chlorine
– Can be purchased in granular, powdered and tablet forms
• Very corrosive, has a strong odour and readily absorbs
moisture and generates chlorine gas
• Should be kept away from organic materials (can generate
heat and cause fire or explosion)
• Packed calcium hypochlorite is very stable
• Can be dissolved in water to prepare a solution with 1-2%
available chlorine and injected as solution
• Tablets of calcium hypo can be directly dissolved in water at
atmospheric pressure
• On dissolution calcium hypochlorite forms OCl- (less effective
as disinfectant than HOCl)

 OClCaOClCa 2)( 2
2
Disinfection by calcium hypochlorite
• Very strong oxidant (comparable to Cl2) and very expensive
• Highly soluble in water (10 times to Cl2)
• React with household materials and produce offensive odours
• Can transfer from solution to gas form and become explosive
• Volatile and subjected to photo-decomposition
• Unstable at higher concentrations (>15%) and under pressure
• Used for disinfection, as primary disinfectant (alternative to Cl2)
• Disinfection is brought about by oxidation
• Does not react with ammonia - Forms halogenated organics and
chlorite (toxic to humans), but not THMs and HAAs
• Superior for manganese oxidation
• Insensitive to pH over a broad range (4-8)
• ClO2 is also used in a pretreatment (>5.0 min contact time)
• Destructs TTHM and HAA precursors, oxidizes manganese and
controls taste and odour (from algae – diatoms)
• Typical dose: 0.6 to 1.7 ppm (2.0 to 5.0 ppm is typical for Cl2)
Disinfection by Chlorine Dioxide
Chlorine dioxide application system
Disinfection by TwinOxide
• Developed and made in Netherlands
• An advanced delivery system of aqueous ClO2 solution (0.3%)
• Delivered as a powder kit of two components having very long shelf
life (5 years)
– Component A: 64% - sodium chlorite and 36% - other ingradients
– Component B: sodium bisulfate
• Components A & B are mixed onsite in specified volume of tap
water at neutral pH , and left for 3 hrs to produce aqueous ClO2
solution (concentrate)
– 4 kg product produces 100 L of 0.3% of the concentrate
– The concentrate should be stored in UV proof sealed container, in cool
dark room (half-life when stored in dark at 22°C is 30-60 days)
• Works as disinfectant in the pH range of 4 to 10
– Imparts no smell, taste or colour
– Generates no chlorine, chlorate, chlorite or chloride
– Non-explosive and lightly corrosive
Disinfection by Chloramines
• Weak disinfectant – effective bactericide but less effective
against viruses and protozoa
– Produces fewer disinfection byproducts (DBPs)
– An effective and appropriate secondary disinfectant
• Formed by chlorinating ammonia containing water or by adding
ammonia (anhydrous ammonia, ammonium sulfate, or
ammonium hydroxide) to the water containing chlorine
– Into the water supply main chlorine is injected and then ammonia
is injected and adequate mixing and contact time is provided
– Chloramines formation reactions are 99% complete within a few
minutes
• Formation of nitrogen trichloride is undesirable
– NCl3 is harmful to humans and imparts disagreeable taste and
odour
– Chlorine to ammonia ratio of 5:1 is not exceeded and pH of water
is not allowed to drop below 5 do not allow NCl3 formation
• Chlorination is highly sensitive to inorganic and organic loads and
forms harmful disinfection byproducts (DBPs), like, tri-halo-
methanes (THMs), halo-acetic acids (HAAs), etc.
• Oxidation products of organics, some are carcinogenic, and some cause
taste and odor problems
• IS 10500: 2012 prescribes limits for total tri-halo-methanes (TTHMs) in
drinking water
• Limits prescribed: 0.08 ppm for TTHM, 0.06 ppm for HAA and 1.0 ppm
for Chlorite
• Factors affecting the DBPs formation
• Types and concentrations of organic materials
• Dose of chlorine and reaction/contact time
• Temperature and pH of water
• Solutions to the disinfection byproducts (DBPs)
• Reducing the organics concentration in the water prior to chlorination
(adsorption on activated carbon)
• Use of alternate disinfectants that form no undesirable DBPs
(substitution of chloramines, a less effective disinfectant, to chlorine)
• Removal of the DBPs formed from the water after chlorination
Disinfection/Chlorination byproducts (DBPs)
Disinfection by Ozonation
• Formed by passing dry air or oxygen through a system of high voltage
electrodes
• Unstable (half life is <15 min.) hence generated onsite
• Ozonation system includes
– Air (or oxygen) preparation as feed (pure oxygen use has higher
production density and requires relatively lesser energy)
– Electrical power supply
– Ozone generation by using a corona discharge cell
– Ozone contact chamber - requires shorter contact time than Cl2
– Ozone exhaust gas destruction
• Used as a primary disinfectant (leaves no disinfecting residue and
hence requires a secondary disinfectant)
– Preferred for waters containing colour and organics
– Has low solubility in water hence needs rigorous mixing
• Capital cost of ozonation systems is higher; Operation and
maintenance is complex; Electricity amounts to 26-43% of O&M cost
• Forms no undesirable products with organics
09 chlorination
Disinfection by UV radiation
• Special lamp is used for UV radiation and disinfection
– Thin sheets of turbidity free water are exposed to UV radiation
(~30 microwatts/cm2)
– Energy intensity and contact time are important
• Destroys genetic material - effective wavelengths is UV-B
• Used as primary disinfectant (attractive for small water
systems)
– May not be effective in inactivating protozoan cysts
– Not suitable for water with high levels of suspended solids,
turbidity, colour and/or soluble organic matter
– A secondary disinfectant must be used to prevent re-growth of
microbes
• Requires shorter contact times - produces no known toxic
residuals
09 chlorination

More Related Content

PPTX
Disinfection
PDF
Water treatment
PPTX
Waster water treatment
PPTX
Primary sedimentation
PPTX
Disinfection Process
PPTX
Water Treatment-Domestic
PPTX
Disinfection&Chlorination
PPTX
Water Treatment Plants
Disinfection
Water treatment
Waster water treatment
Primary sedimentation
Disinfection Process
Water Treatment-Domestic
Disinfection&Chlorination
Water Treatment Plants

What's hot (20)

PDF
L 17 coagulation and flocculation
PDF
L 24 filtration
PPTX
chlorination n chlorine demand
PPTX
2. screen chamber
PPTX
water quality and its parameters
PDF
L 28 disinfection
PPTX
Grit chambers
PPT
Sources of wastewater
PPT
Water Treatment Processes:- Coagulation , Flocculation, Filtration by Kalpesh...
PDF
L 10 sedimentation
PDF
L 8 equalization and proportioning
PPS
Water Quality Control & Treatment
PPT
Coagulation and flocculation in water treatment
PDF
Effluent treatment plant - design, operation and analysis of waste water trea...
PPTX
Disinfection of water
PPTX
Water Treatment Process (Screening)
PPTX
Environmental Engineering
PPT
Characteristics of industrial waste
PPT
Removal of colour and turbidity (coagulation, flocculation filtration)
PDF
L 13 grit chamber
L 17 coagulation and flocculation
L 24 filtration
chlorination n chlorine demand
2. screen chamber
water quality and its parameters
L 28 disinfection
Grit chambers
Sources of wastewater
Water Treatment Processes:- Coagulation , Flocculation, Filtration by Kalpesh...
L 10 sedimentation
L 8 equalization and proportioning
Water Quality Control & Treatment
Coagulation and flocculation in water treatment
Effluent treatment plant - design, operation and analysis of waste water trea...
Disinfection of water
Water Treatment Process (Screening)
Environmental Engineering
Characteristics of industrial waste
Removal of colour and turbidity (coagulation, flocculation filtration)
L 13 grit chamber
Ad

Similar to 09 chlorination (20)

PPTX
ABG_Sewage_Disinfection_Jan 2022.pptx
PPTX
Disinfection.pptx
PPTX
Ee ppt
PPTX
lec3Chemical_disinfectiongoto_of_water.pptx
PPTX
THE METHODS OF DISINFECTION AND THE TYPES OF CHLORINATION
PPTX
THE METHODS OF DISINFECTION AND THE TYPES OF CHLORINATION
PPTX
Disinfection chlorination chlorination derived by products
PPTX
Disinfection
PPT
To manage water discharged from homes, businesses, and industries to reduce t...
PPT
Disinfection theory.ppt
PPT
Disinfection of water - Module 3 VTU syllabus
PPT
Dis211_0203 Disinfection of water as per
PPTX
chlorination.pptx
PPTX
Disinfaction.pptx
PPTX
Alternatives of chlorine, chlorine di-oxide(ClO2) for water treatment
PDF
CHLORINE SAFETY.pdf
PPTX
Disinfection
PPTX
UG - Water Disinfection.pptx
PPT
Chlorine Hazards 2009
PPTX
Disinfection in water treatment plant
ABG_Sewage_Disinfection_Jan 2022.pptx
Disinfection.pptx
Ee ppt
lec3Chemical_disinfectiongoto_of_water.pptx
THE METHODS OF DISINFECTION AND THE TYPES OF CHLORINATION
THE METHODS OF DISINFECTION AND THE TYPES OF CHLORINATION
Disinfection chlorination chlorination derived by products
Disinfection
To manage water discharged from homes, businesses, and industries to reduce t...
Disinfection theory.ppt
Disinfection of water - Module 3 VTU syllabus
Dis211_0203 Disinfection of water as per
chlorination.pptx
Disinfaction.pptx
Alternatives of chlorine, chlorine di-oxide(ClO2) for water treatment
CHLORINE SAFETY.pdf
Disinfection
UG - Water Disinfection.pptx
Chlorine Hazards 2009
Disinfection in water treatment plant
Ad

More from Akepati S. Reddy (20)

PPT
PH,acidity and alkanity
PPT
Td sand tss
PPT
Asr wastewater characteristics
PPTX
Asr flow measurement
PPT
Asr= nutrients
PPT
Asr mp ntest
PPTX
02b priliminary treatment
PPTX
02d secondary treatment
PPTX
Wastewater characteristics
PDF
Chapter2activestudge process
PPT
acticated sluge process
PPTX
Regulatory Requirements of Solid Waste Management, Indian Context
PPTX
Solid waste biomethanation plants
PPTX
Atmospheric Pressure and Winds
PPTX
Atmospheric Water
PPTX
Atmosphere: Composition and Strucutre
PPTX
Radiation and atmospheric temperature
PPT
Biological n and p removal
PPTX
Aerobic attached growth systems
PPT
Biological sludge digestion
PH,acidity and alkanity
Td sand tss
Asr wastewater characteristics
Asr flow measurement
Asr= nutrients
Asr mp ntest
02b priliminary treatment
02d secondary treatment
Wastewater characteristics
Chapter2activestudge process
acticated sluge process
Regulatory Requirements of Solid Waste Management, Indian Context
Solid waste biomethanation plants
Atmospheric Pressure and Winds
Atmospheric Water
Atmosphere: Composition and Strucutre
Radiation and atmospheric temperature
Biological n and p removal
Aerobic attached growth systems
Biological sludge digestion

Recently uploaded (20)

PDF
Parts of Speech Prepositions Presentation in Colorful Cute Style_20250724_230...
PPTX
Understanding-Communication-Berlos-S-M-C-R-Model.pptx
PDF
Enhancing Bambara Groundnut Production Through Improved Agronomic Practices
PPTX
Bob Stewart Journey to Rome 07 30 2025.pptx
PPTX
What is Clause, definition and structure
PPTX
2025-08-03 Joseph 01 (shared slides).pptx
PPTX
Assam' Vibrant Bihu Festival Bihu presentation.pptx
PPTX
DARKWEB Deepweb what to do or not ?.pptx
PDF
Media Training for Authors: Producing Videos & Nailing Interviews
PPTX
Presentation of Project of Enterprenuership topic- "Green Gaurdian"
PPTX
Cohort Study_PPT.group presentation_pdf.pptx
PPTX
IBA DISTRICT PIR PRESENTATION.POWERPOINT
PPTX
CASE PRESENTATION prev 1 lscs[1].pptxgyjgg
PPTX
Role and Responsibilities of Bangladesh Coast Guard Base, Mongla Challenges
PPTX
PHILIPPINE LITERATURE DURING SPANISH ERA
PPT
strucure of protein geomics for new .ppt
PPTX
Caption Text about Social Media Post in Internet
PPTX
Non-Verbal-Communication .mh.pdf_110245_compressed.pptx
PDF
protein structure and function for basics .pdf
PPTX
Selecting relevant value chain/s for Impactful Development Policies
Parts of Speech Prepositions Presentation in Colorful Cute Style_20250724_230...
Understanding-Communication-Berlos-S-M-C-R-Model.pptx
Enhancing Bambara Groundnut Production Through Improved Agronomic Practices
Bob Stewart Journey to Rome 07 30 2025.pptx
What is Clause, definition and structure
2025-08-03 Joseph 01 (shared slides).pptx
Assam' Vibrant Bihu Festival Bihu presentation.pptx
DARKWEB Deepweb what to do or not ?.pptx
Media Training for Authors: Producing Videos & Nailing Interviews
Presentation of Project of Enterprenuership topic- "Green Gaurdian"
Cohort Study_PPT.group presentation_pdf.pptx
IBA DISTRICT PIR PRESENTATION.POWERPOINT
CASE PRESENTATION prev 1 lscs[1].pptxgyjgg
Role and Responsibilities of Bangladesh Coast Guard Base, Mongla Challenges
PHILIPPINE LITERATURE DURING SPANISH ERA
strucure of protein geomics for new .ppt
Caption Text about Social Media Post in Internet
Non-Verbal-Communication .mh.pdf_110245_compressed.pptx
protein structure and function for basics .pdf
Selecting relevant value chain/s for Impactful Development Policies

09 chlorination

  • 2. Biological water quality • Assessed by MPN test • Multiple tube fermentation technique • Membrane filtration technique • Improvement by physical separation or removal of pathogens • Filtration (and membrane filtration, UF!), Coagulation- flocculation, and Settling • Improvement by disinfection: deactivation (render harmless) of pathogens (causing water borne diseases) Disinfection two types • Primary disinfection: achieving desired level of microbial kills or inactivation • Secondary disinfection: maintaining disinfectant residual in finished water to prevent regrowth of microorganisms Biological water quality and Disinfection
  • 3. Disinfectants • Ideal disinfectants – Versatile (effective against all types of pathogens), Fast-acting (effective within short contact times), and Robust (effective in the presence of interfering materials) – Easy to handle (non-toxic, non-flammable, non-explosive , soluble) and Compatible with various materials/surfaces in WTPs (pipes, equipments) – Economical (cheap) – Toxic to microorganisms well below the toxic thresholds to humans and higher animals – Should persist enough to prevent re-growth in the distribution system – Should not form the undesirable disinfection byproducts (DBPs) No disinfectant used is ideal disinfectant
  • 4. Disinfectants • Commonly used disinfectants are – Chemical agents (disinfectants): Chlorine, hypochlorite, Chlorine dioxide (twin oxide) and Chloramines; Ozone; Peroxide, etc. – Irradiation (UV radiation) and Heating (to boiling!) – Sonification, electrocution, etc. • Different disinfectants are effective at different concentrations/ doses • Tolerance levels against a disinfectant are different for different organisms – Cysts, encysted bacteria, bacterial spores, etc. could be more resistant or more tolerant to disinfectant • Factors such as turbidity offer sanctuary and provide shield against disinfection • Disinfectants through reacting with water and its constituents (metals, ammonia, organics, etc.) can form disinfection byproducts (DBPs), and cause taste and odour problems
  • 5. Disinfection kinetics kt N N kN dt dN        0 ln N is the number of microbes ‘t’ is contact time ‘k’ is disinfection rate constant Contact time (Chick’s law) When the disinfectant level is held constant Equal susceptibility and uniform dispersion of the microbes is assumed   21 12 1 2 ln TRT TTE K K a        Disinfection is temperature sensitive Activation energy (Ea) R is gas constant (8.314 J/mol.K) Kills double with 10°C temp. raise Disinfection is function of both time and concentration (C) tCk N N n 0 0 ln Chick-Watson law Disinfection is pH sensitive Ozone is more effective at lower pH Chlorine (OCl-/HOCl) is more effective at lower pH ClO2 is more effective at higher pH
  • 6. Disinfection K0 for 99% kills at 5°C
  • 7. CT values for inactivation using ClO2
  • 8. Chlorination – Chemistry Objectives of chlorination: Disinfection, H2S control, sludge bulking control, odour control, etc. Chlorine as gas and sodium/calcium hypochlorite are used – Large systems use chlorine gas The chlorine based disinfectants release HOCl or OCl- pH and temperature determine the equilibrium relationship – HOCl levels are higher at lower pH (at <5 pH all chlorine is HOCl, 76% HOCl at 7.0 pH, 33% at 7.8 pH and ~0% at >10 pH) – HOCl fraction increases with decreasing temperature Sum of HOCl and OCl- is known as free residual chlorine HOClHOHCl   22   OClCaOClCa 2)( 2 2   OClNaNaOCl   OClHHOCl     HOCl OClH Ka   HOCl is more effective than OCl- as disinfectant
  • 10. Chlorine reacts with reduced materials (Fe2+, Mn2+, H2S, organics, NH3, etc.) Breakpoint Chlorination
  • 11. • Chlorine gas is highly oxidizing, toxic, corrosive and hazardous yellow-green gas (supplied as liquid chlorine in bullets) • Can be lethal to human beings at 0.1% (volume) concentration • Heavier than air and spreads slowly at ground level • Effective against all types of microbes as both primary and secondary disinfectant • Leaves combined and free residual chlorine in the treated water and this can be responsible for secondary disinfection • Chlorine handling requires specialized equipment, care and skill • A separate storage room (not connected to other rooms) with doors opening to outside, and with view windows for inspection • Chlorinator installed in the rooms with direct emergency access to outside air • Self contained breathing apparatus and chlorine cylinder repair kit must be readily accessible • Masks, air tanks, chlorine detection devices etc. needed Disinfection by Chlorine gas
  • 12. • Liquid chlorine is drawn out, vapourized (supply latent heat!) and dosed into water by an injector • Highly pressurized water is passed through a venturi – vacuum created sucks chlorine gas into the water stream • Provisions are made for proper mixing of the chlorine dosed and for the requisite contact time • pH control may be necessary for effective disinfection (chlorine gas on dissolution also reduces the pH) • Alternatively the chlorine gas is dissolved in water to form chlorine solution and this in turn is dosed/injected into water – Solubility is 750 mg/l at usual pH and temperature • Dechlorination of the chlorinated water is often needed for the removal of the residual chlorine – SO2, Na2SO3, sodium metabisulfite, activated carbon can be used Disinfection by Chlorine gas
  • 14. Chlorine dose • Dose range is known from break point chlorination and water flow rates – Water characteristics and residual chlorine desired in water influence the dose • Feedback control involving residual chlorine monitoring is followed Injection and initial mixing • Withdrawn from the bullet as gas and applied either directly or indirectly as aqueous solution – Evaporators are used if withdrawal is >180 kg/day – Evaporators are used for gasification when withdrawal rate is >18 kg/day for 68 kg cylinders and >205 kg/day for 908 kg cylinders • Black steel piping is used for dry chlorine (liquid or gas) conveyance and PVC piping (schedule-80) for chlorine solution • Diffuser (plastic pipe with perforations) is used for chlorine dosing • Mechanical mixing, static inline mixing or hydrodynamic mixing is used for the mixing of chlorine with water Design of chlorination
  • 16. Chlorine contact basin (WHO recommends 15 mg-min/L) • Contact basin is eliminated if travel time of water in the supply pipeline is greater than the needed chlorine contact time • Long plug flow chambers (with 20:1 to 40:1 aspect ratio) are used • Compacted into rectangular tanks with baffles • Hydraulic dead zones and hydraulic short-circuiting are associated with the chlorine contact basins – Submerged baffles, guide vanes and rounded corners are used to avoid the problems Design of chlorination Corrections to C-t Temp. and pH correction Df of contact tank MPN number 6-10% of the total cross-sectional area is openings in the submerged baffles
  • 18. • A separate storage room (not connected to other rooms) with doors opening to outside • Ventilation at floor level to storage chamber with capacity of 60 air changes per hour • Fixed glass viewing window for checking leaks prior to entry • Fan controls at the room entrance • Protect storage and feed facilities from fire hazards • Provide leak detection equipment connected to alarm system • Protect cylinders from direct sun light during summer warm climates • Spill control and containment and emergency caustic scrubbing system to neutralize leaks – Containment vessels to provide total enclosure of cylinder – In the event of cylinder failure gas is contained within and processed at normal rate through chlorination facilities Chlorine storage facilities
  • 19. • More expensive than Cl2 and highly corrosive • Available as a solution with 5-15% available chlorine level • Decomposes on storage – Should not be stored beyond a month and should be stored in cool, dark and dry areas • Easier to handle than calcium hypochlorite and chlorine gas • Preferred for highly populated areas and small scale applications • The sodium hypochlorinator includes a solution tank, dosing pumps, tubing and diffuser – The solution is injected into water supply pipe at controlled rate • On dissolution sodium hypochlorite forms OCl- (less effective as disinfectant than HOCl) • Sodium hypochlorite can be generated onsite by electrolysis of sodium chloride solution (electro-chlorinators!) – Hydrogen is given off here as a byproduct   OClNaNaOCl Disinfection by sodium hypochlorite
  • 20. • A white solid soluble in water and has about 65% available chlorine – Can be purchased in granular, powdered and tablet forms • Very corrosive, has a strong odour and readily absorbs moisture and generates chlorine gas • Should be kept away from organic materials (can generate heat and cause fire or explosion) • Packed calcium hypochlorite is very stable • Can be dissolved in water to prepare a solution with 1-2% available chlorine and injected as solution • Tablets of calcium hypo can be directly dissolved in water at atmospheric pressure • On dissolution calcium hypochlorite forms OCl- (less effective as disinfectant than HOCl)   OClCaOClCa 2)( 2 2 Disinfection by calcium hypochlorite
  • 21. • Very strong oxidant (comparable to Cl2) and very expensive • Highly soluble in water (10 times to Cl2) • React with household materials and produce offensive odours • Can transfer from solution to gas form and become explosive • Volatile and subjected to photo-decomposition • Unstable at higher concentrations (>15%) and under pressure • Used for disinfection, as primary disinfectant (alternative to Cl2) • Disinfection is brought about by oxidation • Does not react with ammonia - Forms halogenated organics and chlorite (toxic to humans), but not THMs and HAAs • Superior for manganese oxidation • Insensitive to pH over a broad range (4-8) • ClO2 is also used in a pretreatment (>5.0 min contact time) • Destructs TTHM and HAA precursors, oxidizes manganese and controls taste and odour (from algae – diatoms) • Typical dose: 0.6 to 1.7 ppm (2.0 to 5.0 ppm is typical for Cl2) Disinfection by Chlorine Dioxide
  • 23. Disinfection by TwinOxide • Developed and made in Netherlands • An advanced delivery system of aqueous ClO2 solution (0.3%) • Delivered as a powder kit of two components having very long shelf life (5 years) – Component A: 64% - sodium chlorite and 36% - other ingradients – Component B: sodium bisulfate • Components A & B are mixed onsite in specified volume of tap water at neutral pH , and left for 3 hrs to produce aqueous ClO2 solution (concentrate) – 4 kg product produces 100 L of 0.3% of the concentrate – The concentrate should be stored in UV proof sealed container, in cool dark room (half-life when stored in dark at 22°C is 30-60 days) • Works as disinfectant in the pH range of 4 to 10 – Imparts no smell, taste or colour – Generates no chlorine, chlorate, chlorite or chloride – Non-explosive and lightly corrosive
  • 24. Disinfection by Chloramines • Weak disinfectant – effective bactericide but less effective against viruses and protozoa – Produces fewer disinfection byproducts (DBPs) – An effective and appropriate secondary disinfectant • Formed by chlorinating ammonia containing water or by adding ammonia (anhydrous ammonia, ammonium sulfate, or ammonium hydroxide) to the water containing chlorine – Into the water supply main chlorine is injected and then ammonia is injected and adequate mixing and contact time is provided – Chloramines formation reactions are 99% complete within a few minutes • Formation of nitrogen trichloride is undesirable – NCl3 is harmful to humans and imparts disagreeable taste and odour – Chlorine to ammonia ratio of 5:1 is not exceeded and pH of water is not allowed to drop below 5 do not allow NCl3 formation
  • 25. • Chlorination is highly sensitive to inorganic and organic loads and forms harmful disinfection byproducts (DBPs), like, tri-halo- methanes (THMs), halo-acetic acids (HAAs), etc. • Oxidation products of organics, some are carcinogenic, and some cause taste and odor problems • IS 10500: 2012 prescribes limits for total tri-halo-methanes (TTHMs) in drinking water • Limits prescribed: 0.08 ppm for TTHM, 0.06 ppm for HAA and 1.0 ppm for Chlorite • Factors affecting the DBPs formation • Types and concentrations of organic materials • Dose of chlorine and reaction/contact time • Temperature and pH of water • Solutions to the disinfection byproducts (DBPs) • Reducing the organics concentration in the water prior to chlorination (adsorption on activated carbon) • Use of alternate disinfectants that form no undesirable DBPs (substitution of chloramines, a less effective disinfectant, to chlorine) • Removal of the DBPs formed from the water after chlorination Disinfection/Chlorination byproducts (DBPs)
  • 26. Disinfection by Ozonation • Formed by passing dry air or oxygen through a system of high voltage electrodes • Unstable (half life is <15 min.) hence generated onsite • Ozonation system includes – Air (or oxygen) preparation as feed (pure oxygen use has higher production density and requires relatively lesser energy) – Electrical power supply – Ozone generation by using a corona discharge cell – Ozone contact chamber - requires shorter contact time than Cl2 – Ozone exhaust gas destruction • Used as a primary disinfectant (leaves no disinfecting residue and hence requires a secondary disinfectant) – Preferred for waters containing colour and organics – Has low solubility in water hence needs rigorous mixing • Capital cost of ozonation systems is higher; Operation and maintenance is complex; Electricity amounts to 26-43% of O&M cost • Forms no undesirable products with organics
  • 28. Disinfection by UV radiation • Special lamp is used for UV radiation and disinfection – Thin sheets of turbidity free water are exposed to UV radiation (~30 microwatts/cm2) – Energy intensity and contact time are important • Destroys genetic material - effective wavelengths is UV-B • Used as primary disinfectant (attractive for small water systems) – May not be effective in inactivating protozoan cysts – Not suitable for water with high levels of suspended solids, turbidity, colour and/or soluble organic matter – A secondary disinfectant must be used to prevent re-growth of microbes • Requires shorter contact times - produces no known toxic residuals