Chapter 8-Filtration (56 P)

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    PART III. CASE STUDIES

    Chapter 8. Filt ration

    1

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    Characteristics

    1) Filtration used for removal of suspended and colloidal solids.

    Coa-Floc-Sed followed by filtration

    Direct filtration

    Direct filtration of high solids

    2) Porous media captures solids and transports water.

    Solid: suspended vs. dissolved?

    Capture dissolved solids?

    3) Filtration is primary a physical process but chemicals can be added to improve

    performance.

    2

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    3

    10-3um, < colloids < 1 um

    1 um < suspended solids < 103um

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    Characteristics

    4) Two phase process: Solids removal during filtration followed by solids removal

    (backwashing).

    5) Because it is a two phase process, filtration is typically discontinuous but some

    filters are designed to simultaneous filtration and backwashing. Alternatively, you can

    design several filtration units in parallel.

    - Membrane filtration or separation is excluded in this chapter.

    4

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    General Classif ication of f ilters According to the Types of Media

    1)Single Medium Filters

    -One type of medium

    -Typically sand or crushed anthracite coal

    2) Dual-media filters

    -Two types of media

    -Typically crushed anthracite and sand

    3) Multimedia filters

    -Three types of media

    -Typically crushed anthracite, sand, and garnet

    5

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    General Classification of Filters According to Filtration Principles

    1) Granular medium filtration.

    - Rapid sand filters

    2) Surface filtration

    - Micro-screens- Vacuum filters/Pre-coat filters

    - Slow sand filters

    6

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    Desired characteristics of the Perfect filter

    1)2)

    3)

    4)

    5)

    6)

    7

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    Definition sketch for length of filtration run.

    8

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    Granular Medium Filtration (Rapid Sand Filtration (vs. slow sand fil tration))

    Classification

    1) Flow direction

    - Downflow

    - Upflow

    - Biflow

    9

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    10

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    11

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    Granular Medium Filtration

    Classification

    2) Types of Filtering Materials & Filter Configurations.

    12

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    Classification

    3) Driving Force

    -Gravity

    -Pressure

    13

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    Classification

    4) Flow Control

    14

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    Classification

    5) Backwash/Surface Wash

    15Operation of conventional downflow, granular-medium, gravity-flow filter

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    16

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    17

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    18Removal of Suspended Particulate Matter with a Granular Filter

    Straining

    Sedimentationor inertial impaction

    Interception

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    19

    Removal of Suspended Particulate Matter with a Granular Filter

    Adhesion

    Flocculation

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    20

    Solids Removal in Depth Filtration

    It is important to realize that particles that contact the media surface must attach or

    bond to the surface, with the exception of particles removed by straining. The

    bonding forces in filtration are the same as those on coagulation and flocculation:

    van der Waals forces. It is also possible that particles will be sheared off or detach

    from the media, but reattach deeper in the filter.

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    21

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    == .CoeffUniformityUC

    Grain size and distribution

    Effective size = D10

    However, grain shape is also an important factor in calculating filtration headlosses and

    bed expansion during bachwashing.

    22

    D10

    If D10and CU are small, ??? (vice

    versa)

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    grainsandofareasurfaceactual

    deqwithspherevolumeequalofareasurfaceDefine sphericity, =

    Grain density: affects mostly ??

    Grain hardness: affects mostly ??

    23

    In the absence of determining dequse the mean diameter between sieves as an

    approximation of deq.

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    ==volumebedTotal

    volumeVoidPorosityBedFixed

    hrmhrm

    mton

    AreaSurface

    FlowmediaofrateFiltration /

    )(, 2

    3

    =

    =

    24

    , head-loss but water quality

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    25

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    26

    day

    ftgalFiltrationSand

    /180m

    7.5m/hr

    hr/m7.5m

    hrL/m7500

    min/3,

    3

    23

    2

    2

    =

    =

    =

    =

    watertonorm

    population

    personperL

    3000,500

    000,000,1

    500

    )176176(5353

    2778180

    000,500 2

    ftftormm

    mrequiredareaFiltration

    =

    ==

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    Hydraulics of depth fi ltration flow

    27

    Darcys Law Laminar flow

    Divided by A

    KSX

    hKqAQ =

    ==/

    Darcys law can be applied for the hydraulics to estimate how much water can be

    transported away from the site

    Darcys law: a phenomenologically derived constitutive equation that describes the

    flow of a fluid through a porous medium.

    http://en.wikipedia.org/wiki/File:Darcy%27s_Law.png
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    KSX

    hKq =

    =

    Darcys Law

    q = hydraulic flux, or velocity of flow (apparent velocity, Va), m/d

    K = permeability coefficient or hydraulic conductivity, m/d

    h = head-loss (or pressure drop)

    X = distance where the head-loss occurs

    S = hydraulic gradient, m/m

    28

    Laminar flow in Circular Pipes (Void Space)

    VD

    L

    gVD

    L

    hL 22 3232

    ==

    L

    hgDV L

    32

    2

    =

    weightspecificg==

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    KSX

    hKq =

    =

    29

    Laminar flow in Circular Pipes (Void Space)

    VD

    L

    ghL 232

    =

    What happens in Circular Pipes (Channel) with

    Medium

    ?????32 2VD

    L

    ghL

    =

    http://en.wikipedia.org/wiki/File:Darcy%27s_Law.png
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    Apply the equation now to flow through porous media.

    Consider media is composed of spheres and voids.

    = Porosity

    T

    V=

    V= Void volumeT= Total volume

    30

    L32

    hgDV L

    2

    a

    =

    Face velocity = Vapparent= Va

    Va=V

    V = average velocity through pores

    dP,4

    dA,

    P

    AR

    2

    H =

    ==

    Relating D to the hydraulic radius, RH

    For a pipe flowing full D=4RH

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    L32

    hgDV L

    2

    a

    =

    Relating D to the hydraulic radius, RH

    For voids & spheres

    spheresofareasurface

    volumevoid

    AR

    R

    LA

    LR

    LA

    LP

    LAR

    S

    VH =

    =

    =

    =

    =

    244

    244

    2

    TV =

    ( )== 1

    TVTS

    = 1S

    T

    31

    S

    SH

    AR

    =

    1

    SV

    =

    1

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    ( )L

    hR

    gV LHa

    24

    32

    =L

    hR

    g LH

    2

    2

    =

    ( )

    2

    2

    3

    12

    =

    S

    SLa

    ALhgV

    ( )a

    S

    SL LV

    A

    g

    h

    2

    3

    212

    =

    6,

    3

    2 S

    SS

    ddA

    ==

    SS

    S

    dV

    ASdefine 6

    ==

    For non-sphereseqd

    S

    6=

    32

    S

    SH

    AR

    =

    1

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    ( ) LVd

    )'S(1

    g

    2h a2

    S

    2

    3

    2

    L

    =

    S' = 6 for spheres

    Finally

    This is essentially the Fair- Hatch eq.

    In AWWA it is called the Kozeny equation.

    33

    seqs

    s

    d

    S

    dV

    AS

    '6===

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    ( )g

    V

    d

    L1fh

    2a

    3

    =

    dVNwhere

    NVfbut a

    a

    == ReRe

    641

    Other equations developed f rom theoretical considerationsCarmen Kozeny based on Darcy-Weisbach

    34

    ( )LV

    d

    )'S(1

    g

    2h a2

    S

    2

    3

    2

    L

    =

    Friction factor

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    35

    Headloss Equations Summary

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    ( ) ( ) 23223

    2

    Vd

    L

    e

    e1

    g

    75.1V

    d

    L

    e

    e1

    g150h

    +

    =

    ( ) ( ) ( ) 23223

    2

    Vdeq

    L

    e

    e1

    g

    88.274.1V

    deq

    L

    e

    e1

    g150h

    +

    =

    ( )V

    d

    L

    e

    e1

    g180h

    223

    2

    =

    ( )V

    deq

    L

    e

    e1

    g180h

    223

    2

    =

    Headloss Equations Summary

    Carmen Kozeny M&E

    Ergun AWWA

    Kozeny AWWA

    Fair-Hatch M&E

    36

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    BGD FFF =

    Backwashing Hydraulics (Recall Chapter 7 for Particle Settling)

    When particles are completely fluidize; i.e. no particles are touching (Discrete)

    ( ) PWSsp

    wPD gV

    AC = 2

    2

    Vb = Backwash velocity m/s

    37

    DBGT FFFF =0

    eeL ,

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    Backwashing Hydraulics

    ( )2

    22

    2

    22

    2

    22

    1

    2 b

    spb

    wPDb

    b

    spwPDPWS

    sp

    wPD V

    VVAC

    V

    VVACg

    VAC ===

    Vb = Backwash velocity m/s

    38

    eeL ,

    (e) = Correction factor to relate backwash velocity to

    the discrete particle settling velocity, Vsp

    PWSe

    b

    wPDb

    spb

    wPD

    gVV

    ACV

    VVAC )()(

    22

    2

    2

    22

    ==

    )()( 2 eb

    sp

    V

    V=

    B k hi H d li

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    Backwashing Hydraulics

    ( ) ( ) PWSeb

    wPD gV

    AC = 2

    2

    ( )

    =

    P

    P

    WD

    WPsp

    AC

    g2V

    Recall V For a sphere (Chapter 7)

    39

    laminar.,.24

    1

    Re

    Re ei

    N

    CNfor D