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    Sludge Treatment and Disposal - 1

    Mohamed Hasnain Isa

    Civil Engineering Department

    Universiti Teknologi PETRONAS31750 Tronoh, Perak, Malaysia

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    Able to manage biosolids resulting fromtreatment of water and wastewater.

    Able to apply engineering principles to design

    water and wastewater treatment processes.

    Able to identify/solve water and wastewater

    problems (domestic and industrial)..

    Learning Outcomes 2, 3, 5, 6

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    Objectives

    To identify the sources and characteristics of

    water and wastewater sludges.

    To explain methods for sludge thickening.

    To analyse and design gravity sludge thickener.

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    Sources and Characteristics of Solids and Sludgesdepend on the type of plant and method of operation

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    Sludge Thickeningphysical process

    increases the concentration of solids of sludge

    reduces sludge volume to facilitate ease in handling,

    treatment and disposal

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    99

    Table Recommended hydraulic overflow rates for

    gravity thickeners

    Type of sludge Max. overflow rate, m3/m2.d

    Primary 15.5-31

    Waste activated sludge 4-8

    Combined primary and

    waste activated sludge

    6-12

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    1010

    Sludge discharge

    Scraper blades

    Sludge influentSlats/pickets

    Inlet baffle

    Supernatant

    overflow

    Sludge discharge

    Scraper blades

    Sludge influentSlats/pickets

    Inlet baffle

    Supernatant

    overflow

    Figure Gravity sludge thickener

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    1111

    Figure Gravity sludgethickener (partially filled)

    Figure Gravity sludgethickener (empty)

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    Table Typical sludge concentrations and solid loading for

    gravity thickeners

    Type of sludge Solids concentration, % Solids loading

    Unthickened Thickened kg/m2.d

    Separate:

    Primary sludge 2-6 5-10 100-150

    Trickling filter 1-4 3-6 40-50RBC 1-3.5 2-5 35-50

    Air-ASP 0.5-1.5 2-3 20-40

    High purity oxygen-ASP 0.5-1.5 2-3 20-40

    Extended aeration-ASP 0.2

    -1.02

    -32

    5-4

    0Anaerobically digested primary

    sludge from primary digester

    8 12 120

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    Type of sludge Solids concentration, % Solids loading

    Unthickened Thickened kg/m2.d

    Combined:

    Primary and trickling filter 2-6 5-9 60-100

    Primary and RBC 2-6 5-8 50-90

    Primary and waste activatedsludge

    0.5-1.5 4-6 25-70

    2.5-4.0 4-7 40-80

    Trickling filter and waste

    activated sludge

    0.5-2.5 2-4 20-40

    Chemical (tertiary):

    High lime 3-4.5 12-15 120-300

    Low lime 3-4.5 10-12 50-150

    Iron 0.5-1.5 3-4 10-50

    contd.

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    Figure Suspended solids and BOD removal as a function

    of surface overflow rate

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    1515Figure Excessive sludge production v. F/M ratio

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    Dissolved Air Floatation

    air is forced into solution under pressure and then mixed

    with sludge in the influent

    the mixture enters a floatation tank and the rising air

    bubbles carry the sludge flocs to the liquid surface

    the layer of thickened sludge formed on the liquid surfaceis skimmed off

    the skimmed effluent exits as underflow

    sludge can be thickened to about 6 % solids by floatation

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    thickening of solids by floatation is primarily influenced by

    air-to-solids ratio, sludge characteristics (in particular the

    SVI), solids loading rate and polymer application

    the air-to-solid ratio at which the float solids are maximised

    ranges from 2 to 4 %

    good thickening has been observed with SVI less than

    200

    higher loadings can be used with dissolved air floatation

    than gravity thickeners due to the rapid separation of solids

    from the wastewater

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    Influent

    Sludge

    Pressurized

    air

    Effluent

    Sludge skimming

    Rising air bubbles

    with sludge

    Influent

    Sludge

    Pressurized

    air

    Effluent

    Sludge skimming

    Rising air bubbles

    with sludge

    Figure Sludge thickening by dissolved air floatation

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    Table Typical solids loadings for sludge thickeners using

    dissolved air floatation

    Type of sludge Solids loading, kg/m2.h

    Without chemical

    addition

    With chemicals

    addition

    Air-ASP:

    Mixed liquor 1.2-3.0 Up to 10Settled 2.4-4.0 Up to 10

    High purity oxygen-ASP 3.0-4.0 Up to 10

    Trickling filter 3.0-4.0 Up to 10

    Primary and air ASP 3.0-6.0 Up to 10

    Primary and trickling filter 4.0-6.0 Up to 10

    Primary sludge only 4.0-6.0 Up to 12.5

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    2020

    a

    a

    SfPs

    SA )1(3.1

    !

    where

    A/S = air to solids ratio, mL (air)/mg (solids)sa = air solubility, mL/L

    f = fraction of air dissolved at pressure P, usually 0.5

    P = pressure, atm =

    Sa = influent suspended solids, mg/L

    35.101

    35.101p

    If entire flow is pressurised,

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    QSRfPs

    SA

    a

    a )1(3.1

    !

    where

    R = pressurised recycle, m3

    /dQ = mixed liquor flow, m3/d

    If only recycle is pressurised,

    Temp., C 0 10 20 30

    sa, mL/L 29.2 22.8 18.7 15.7

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    2222

    Q.1 The flow diagram for a wastewater treatment plant is as

    shown below. The following information is also given:

    Treatment plant:Diameter of PST = 20 m

    Volume of aeration tank = 2 500 m3

    MLSS in aeration tank = 3 000 mg/l

    Wastewater:

    Influent suspended solids = 220 mg/l

    Influent BOD = 250 mg/l

    Effluent BOD = 20 mg/l

    Flow = 20 000 m3

    /d

    Sludge solids:

    Primary sedimentation tank = 3.5 %

    Secondary sedimentation tank = 0.8 %

    Gravity thickener = 5 %

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    Determine:

    (i) the mass and volumetric loading rates to the thickener.

    (ii) the percent volume reduction by the gravity thickener.

    Primary

    Sedimentation

    Tank

    Secondary

    Sedimentation

    TankAeration Tank

    EffluentInfluent

    Gravity

    Thickener

    Return liquid

    Thickened sludge

    disposal

    Return sludge

    Primary

    Sedimentation

    Tank

    Primary

    Sedimentation

    Tank

    Secondary

    Sedimentation

    Tank

    Secondary

    Sedimentation

    TankAeration TankAeration Tank

    EffluentInfluent

    Gravity

    Thickener

    Gravity

    Thickener

    Return liquid

    Thickened sludge

    disposal

    Return sludge

    Primary

    Sedimentation

    Tank

    Secondary

    Sedimentation

    TankAeration Tank

    EffluentInfluent

    Gravity

    Thickener

    Return liquid

    Thickened sludge

    disposal

    Return sludge

    Primary

    Sedimentation

    Tank

    Primary

    Sedimentation

    Tank

    Secondary

    Sedimentation

    Tank

    Secondary

    Sedimentation

    TankAeration TankAeration Tank

    EffluentInfluent

    Gravity

    Thickener

    Gravity

    Thickener

    Return liquid

    Thickened sludge

    disposal

    Return sludge

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    Q.2 Design a gravity thickener for a wastewater treatment

    plant with the following sludge characteristics:

    Type of sludge Specific gravity Solids

    %

    Flow rate

    m3/d

    Average design conditions:

    Primary sludge 1.03 3.3 400

    Waste activated 1.005 0.2 2250

    Peak design conditions:

    Primary sludge 1.03 3.4 420

    Waste activated 1.005 0.23 2500

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    Q.3 Design a floatation thickener without and with pressurised

    recycle to thicken the solids in an activated sludge mixed

    liquor from 0.2

    to4%. The following conditions apply:

    Optimum A/S ratio = 0.012 mL/mg

    Temperature =2

    0 CAir solubility = 18.7 mL/L

    Recycle system pressure = 280 kPa

    Fraction of saturation = 0.5

    Surface loading rate = 9 L/m2.min

    Sludge flow rate = 500 m3/d

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    Q4.

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    Thank you