Water Treatment Overview [Read-Only]

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    Water Treatmentater TreatmentProf.(Mrs.) Niranjanie RatnayakeDepartment of Civil Engineering

    U i it f M tniversity of Moratuwa

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    a a uwawa eservo r

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    Need for Treatment

    Water needs to be treated if the quality ofthe water does not satisfy the objectivewater quality of the intended use.

    The treatment process should bedesigned taking into consideration theesigned taking into consideration theraw water quality and the objective waterquality.y If the water is to be used for domesticwater supply, the objective water quality

    h ld ti f th N ti l St d d fhould satisfy the National Standards forDrinking Water Quality, which arestipulated based on the WHO Guidelines.29/05/02 3

    stipulated based on the WHO Guidelines.

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    Quality Objectives of Domesticuality Objectives of DomesticWater Supply To protect the health of the community

    Treated water must be free from Pathogenic micro organisms Harmful organic and inorganic chemical substances

    To supply a product which is aestheticallyo supply a product which is aestheticallydesirable Treated water must havereated water must have

    Pleasant taste, odour, colour Low turbidity

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    (Plain Sedimentation)

    Flocculation

    Filtration

    Stabilization

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    water

    Purpose: Addition of O

    Oxidize Fe and Mn

    Removal of CO2

    Make water palatable

    Reduce corrosion

    Removal of H2S, NH3,CH4

    so en ng

    Control of taste,

    odour, corrosion,

    Removal of volatile gaseseffects on cementand concrete etc

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    T es of Aerators

    Gravit Aerators

    Cascades

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    Types of Aerators(contd.)

    Spray Aerators

    Stationary Moving

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    Plain Sedimentation This process is necessary when water

    contains much heavy suspended

    particles, that would settle underquiescent conditions.

    This step can be omitted if the source is a

    reservoir or groundwater.

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    Coagulation and FlocculationPurpose: To destabilize the colloidal particles

    particles which would be heavy enough tosettle under uiescent conditions

    Coagulation: addition of chemicals to destabilizethe colloids. Rapid mixing is important.

    Common Coagulants:

    um n um a s Ferric Salts

    Polyelectrolytes

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    oagu a on an occu a on con .

    the destabilized suspension toallow particles to adhere to

    each other. It is important that

    a velocity gradient is created

    between articles in the water.

    This is achieved by slow

    stirring or creating a head loss

    .

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    Sedimentation

    Particles having high settling velocity willbe removed.

    In sludge blanket clarifiers, particles are

    removed b tra in within the slud eblanket.

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    Sedimentation Tanks Clarifiers

    HorizontalFlow Tank

    Circular Tank

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    Coagulation, Flocculation and

    Sedimentation

    oagu an s a e o e rap m xer a e n e

    end Paddle flocculators provide slow mixing

    The floc particles are settled in the sedimentationtank.

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    Kalatuwawa

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    Purpose is to improve

    turbidity by removingsuspended and colloidal

    par c es.

    Granular Bed Filters Rapid Sand Filters

    Pressure Filters

    Water to be filtered

    Gravel - support

    an - er me um

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    Under drainage

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    -Filter

    Filter tray

    Filter Sand

    Graded

    gravel

    Filter floorCast iron

    Perforatedlaterals

    Filter floor

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    Slow Sand Filters First type of filter in UK

    Cleaning: by scraping top 5-8 cm of sandafter 4 6 weeks

    unc on ng: stratified bed

    Formation of schmutzdecke Removes suspended matter by straining

    and dissolved organics by biological activity

    Some removal of bacteria

    Limitations: Low rate of flow requires large area

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    Slow Sand Rapid Sand

    Flow rate (m/h) 0.1 to 0.3 5 to 10

    Depth of supernatant

    water (m)

    1 to 1.5 1 to 1.5

    (m)

    . . .

    Effective size of sand 0.15 to 0.35 0.45 to 0.55

    Uniformity coefficient 1.8 to >2.5 1.2 to 1.7

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    Effective Size= sieve size of 10% passing; Uniformity Coeff. =size

    size

    %10

    %60

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    s n ec on

    Process of destroying or inactivationof atho enic microor anisms.

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    Ability to destroy pathogens at

    concentrations likely to occur in water Not toxic to man and other animals

    Have a residual disinfectant capacity

    Safe, easy to handle, economical Easy to control and detect in water

    Chlorine gas NaOCl

    Ca(OCl) 2ClO2

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    2

    Powder)

    zone

    UV Radiation

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    Chlorine Disinfection

    Chlorine gas is available as liquid chlorine

    in pressurized cylinders.

    Bleaching powder should be dissolved in

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    Ozone Disinfection Advantages:

    No taste or odour problems Produced from air, which is in abundant supply

    n epen en o p

    No known toxic products

    Limitations Higher cost

    Cannot be applied directly to existing plants

    Efficient Ozone roduction and a lication

    methods need to be developed Disinfection affected by competing impurities

    No lon term rotection needs ost-chlorination

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    Advantages: Simple to use

    Minimum space requirement

    No changes in characteristics of the water

    No residuals

    Limitations Water should not be turbid, coloured or contain

    dissolved organics

    No residuals to fight any subsequent contamination

    PHOTO REACTIVATION reactivation of pathogens atlow energy doses.

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    Adjustment of the pH and alkalinity of the

    water, so that

    It would not dissolve calcium carbonate

    coa ngs rom p pes

    Nor precipitate out calcium carbonate and

    la down de osits that clo i es.

    This is the final ste in Conventional

    Water Treatment.

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    These are done for specific purposes Water Softening

    Iron and Manganese Removal

    e.g. softening

    Membrane processes Reverse Osmosis

    Ultrafiltration

    Adsorption - for removal of colour, taste,odour etc.

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