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    Sedimentation Process

    It is the removal of solid particles from suspension by settling under gravity.

    Sedimentation process is used for the removal from water discrete particles, flocculatedmatter, and precipitation formed during various water treatment operations.

    Classification of Settling Behaviour/Categories of Sedimentation Process

    i.

    Unhindered of discrete particles

    ii.

    Settling of dilute suspension of flocculent particles.

    iii.

    Hindered / zone settling

    iv.

    Compression settling or compaction settling

    The above could be referred to as four classes of settling behaviour of particles.

    Settling Of Discrete Particles

    A discrete particle moving vertically downward through a quiescent fluid will accelerate until

    the frictional resistance of drag of the fluid equals the impelling force acting upon the

    particle, particle then settles at a uniform velocity.

    Vp= particle settling velocity (m/s)

    d = the drag force

    w = submerged weight of the particle

    d = the diameter of the particle (m)

    Ap = projected area of particle normal at direction of motion (m2)

    p = volume of particle (m3)

    = density of particles (kg/m3)

    f = fluid density (kg/m3)

    = dynamic viscosity of fluid (N.s/m2).

    Figure 1: An idealized spherical particle

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    CD= drag coefficient

    To find an expression for Vp (particle settling velocity);

    Drag force on the particle is given:

    D = CD Ap2

    2

    pV................ eqn 1

    Taking the submerged weight of particles as:

    w = (p -f)g p .................. eqn 2

    Substitute for Ap and p , and re-arranging by equating equations 1 and 2

    Vp= Ddf Cg /3/4

    Drag coefficient CD is a function of the Reynolds number (Re). Re for spherical particle

    therefore:

    i. Re< 1, CD= 24/Re

    ii.

    For 1 < Re

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    i. Particles diameter

    ii. Particles density

    iii. Fluid viscosity

    iv. Temperature

    In practical sedimentation tanks, the terminal settling velocity is reached quickly, discrete

    particlesand in uniform fluid flow; the settling velocity is constant throughout the settling

    time.

    Sedimentation in an Ideal Tank

    In ideal rectangular horizontal flow sedimentation:

    i. Inlet zone where water is distributed along the cross-section.

    ii.

    A settling zone which removes suspended particles and is in a quiescent state.

    iii. A sludge zone which collects settled particles.

    iv. An outlet zone through which water along with non-settleable particles is carried

    outside the tank.

    The critical particle for design purpose is that one that enters at the top of the settling zone at

    point A.

    It settles with velocity just sufficient to reach the sludge zone at the outlet end of the tank at

    point B.

    Velocity components of such a particle = Vh in the horizontal direction, while Vp (theterminal settling velocity) is in the vertical direction.

    Time require for the particle to settle, considering the geometry of the tank i.e. detention

    time.

    to=Vh

    L

    Vp

    H

    Note:Vh (velocity in the horizontal direction) = Q/WH

    Vp= Q/WL (Surface Area)

    Q = flow rate

    L = length of tank

    W= width of tank

    H = depth of tank

    Note: the surface area of the tank (A) = W * L

    Hence Vp=Q/WL = Q/A

    [Vp = Q/A]-the termi nal settli ng velocity whi ch is also the sur face loading rate or overf low rate.

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    Figure 2: Types of Sedimentation tanks

    For any particle to settle in an ideal sedimentation tank; a settling velocity of Q/Ais essential.

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    Note: (Q/A) = the surface loading rate or overflow rate is a fundamental parameter governing

    sedimentation tank performance.

    Sedimentation efficiency is independent of tank depth (under the condition that the froward

    velocity is low enough to ensure that settled materials is not scoured and re-suspended fromthe tank floor.

    Circular Radial Flow Tank

    Same relationship as affects ideal rectangular tank applies here (See figure).

    Vp = Q/A, Vp= terminal settling velocity

    Detention time: to= H/Vp

    to= 2

    1

    R

    R hvr

    Since Vr=rH

    Q

    2

    Then, t = 2

    1

    .2 R

    Rdrr

    Q

    H

    = Q

    HRR 2

    1

    2

    2

    Since, r 21

    2

    2 RR = A, hence

    Q

    AH

    V

    H

    p

    Vp A

    Q

    Ideal Upflow Sedimentation Tank

    Particle will only be removed if the settling velocity (Vp) exceeds the upflow velocity of

    water.

    Minimum upflow velocity is represented by (Q/A) (flowrate / surface area)

    The minimum settling velocity needed equals Q/A). See Figure 1c

    Particle remover occurs when Vu= Q/A

    Vp= Vu

    Also: Vp= Q/A

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    Note:

    (i) In ideal sedimentation tank, horizontal or radical flow pattern:

    -

    Particles with settling velocity less than: Vp= Q/A, i.e.n

    Vp , will also be removed in

    the proportion (1/n).

    (ii) In ideal upflow tank, particle with settling velocityA

    Qp will be removed.

    We have just treated the first class of settling, unhindered settling of discrete particles. The

    remaining three are:

    i. Settling of dilute suspension of flocculent particles.

    ii.

    Hindered/ zone settling

    iii. Compression or compaction.

    Class II: Settlement of Dilute Suspension of Flocculent Particles

    This class of settling behaviour is for organic waste matter, biological solids, and flocculated

    impurities.

    Sedimentation Process:i.

    Variety of particles sizes settle at different rates, larger particles settle first,

    overtaking, slower settling particles.

    ii.

    Colliding particles coalesce to form larger particles with increased settling

    velocity

    i i i . Depth should be greater enough to provide the opportunity for particle

    agglomeration to occur. Hence, sedimentati on tanks for f locculent suspension

    must have depth consideration.

    iv. Detention time (t) =Q

    WLH

    Q

    , note WL = Area (A)

    = volume of settling zone (m3)

    Q = flow rate (m3/s)

    Detention time (t) =Q

    AH,

    AQ

    Hwhere L, W, and H are length and the depth of

    the tank.

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    Figure 3: Settling path in an ideal settling tank

    Class III: Hindered Settling, Zone Settling and Sludge Blanket Clarifiers

    Class three setting behaviour occurs with increasing particles concentration in suspension.

    i. There is a reduced particle-settling velocity due to display of velocity field of the

    fluid by adjacent particles overlap.

    ii. There is also a reduced particle settling velocity known as hindered settl ing

    iii.

    When the whole suspension tends to settle as a blanket under extreme particleconcentration, it is known as zone settl ing.

    Class IV: Compression or Compaction Settling

    This class of settling behaviour occurs due to extreme condition of high particle

    concentration.

    Compressed particles get settled under the weight of overlying solids, with decrease in void

    spaces with a corresponding squeezing of water out of the matrix. Compression settling is

    very important in gravity thickening processes.