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Bahan Modeling 04 [Compatibility Mode]

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  • Model Streeter - Phelps

  • Effect of Organic Wastes on Stream Ecosystems StreeterStreeter--Phelps Model Phelps Model DO sag curveDO sag curve

    Many equations and computer programs are available Many equations and computer programs are available today to describe the quality of water in streams, rivers today to describe the quality of water in streams, rivers and lakesand lakesand lakesand lakes

    The most prevalent is the Streeter Phelps equation. The most prevalent is the Streeter Phelps equation. Addition of wastewater (BOD) typically causes a slow Addition of wastewater (BOD) typically causes a slow

    decrease in Odecrease in O22, followed by a gradual increase close to , followed by a gradual increase close to the dissolved oxygen (D.O.) saturation concentrationthe dissolved oxygen (D.O.) saturation concentration

  • Streeter-Phelps Model Assumptions of the ModelAssumptions of the Model

    stream is an ideal plug flow reactorstream is an ideal plug flow reactor steadysteady--state flow and BOD and DO reaction state flow and BOD and DO reaction steadysteady--state flow and BOD and DO reaction state flow and BOD and DO reaction

    conditionsconditions The only reactions of interest are BOD The only reactions of interest are BOD

    exertion and transfer of oxygen from air to exertion and transfer of oxygen from air to water across airwater across air--water interfacewater interface

  • Streeter-Phelps Model Mass Balance for the ModelMass Balance for the Model

    Not a SteadyNot a Steady--state situationstate situationrate Orate O2 2 accum. = rate Oaccum. = rate O22 in in rate Orate O22 out + prod. out + prod. cons.cons.rate Orate O2 2 accum. = rate Oaccum. = rate O22 in in 0 + 0 0 + 0 rate Orate O22 cons.cons.

    Both reoxygenation and deoxygenation are 1Both reoxygenation and deoxygenation are 1stst orderorderrate of deoxygenation = rate of deoxygenation = --kk11CCkk11= deoxygenation constant, function of waste type and = deoxygenation constant, function of waste type and

    temperaturetemperature

  • Streeter-Phelps Modelrate of reoxygenation = krate of reoxygenation = k22DDD = deficit in D.O. or difference between D = deficit in D.O. or difference between

    saturation and current D.O.saturation and current D.O.kk22 = reoxygenation constant= reoxygenation constant

    [ ]( )2

    3

    21)20(21

    2025.19.3

    H

    vkT

    =

  • Streeter-Phelps Model

    WhereWhereT = temperature of water, T = temperature of water, CCH= average depth of flow, mH= average depth of flow, mH= average depth of flow, mH= average depth of flow, mv = mean stream velocity, m/sv = mean stream velocity, m/s

    Oxygen DeficitOxygen DeficitD = S D = S CC

    D.O. deficit = saturation D.O. D.O. deficit = saturation D.O. D.O. in the waterD.O. in the water

  • Streeter-Phelps Model

  • Streeter-Phelps Model

    Deoxygenation rate is equivalent to BOD of Deoxygenation rate is equivalent to BOD of wastewaste

    rro o = k= k11 LLtt rro o = k= k11 LLttLLtt = L= Looee--KtKt

    LLoo or L = ultimate BOD of the wastewater and or L = ultimate BOD of the wastewater and stream water mixturestream water mixture

  • Streeter-Phelps Model

    In terms of the deficit with timeIn terms of the deficit with time

    tkLez

    DkzkdtdD

    1

    21

    =

    =

  • Streeter-Phelps Model Substiting and integrating yields the following Substiting and integrating yields the following

    equationsequationstk

    o

    tktko eDeekk

    LkD 221 )(1 +

    =

    kk 12

    tkoc

    tko

    eLkkD

    DkeLkdtdD

    1

    1

    2

    1

    21 0

    =

    ==

    =

    o

    oc Lk

    kkDkk

    kkt

    1

    12

    1

    2

    12

    )(1ln1

  • Streeter-Phelps Model Example:Example:

    Wastewater mixes with a river resulting in aWastewater mixes with a river resulting in aBOD = 10.9 mg/L, BOD = 10.9 mg/L, DO = 7.6 mg/LDO = 7.6 mg/LThe mixture has a temp. = 20 The mixture has a temp. = 20 CCThe mixture has a temp. = 20 The mixture has a temp. = 20 CCDeoxygenation const.= 0.2 dayDeoxygenation const.= 0.2 day--11Average flow = 0.3 m/s, Average flow = 0.3 m/s, Average depth = 3.0 mAverage depth = 3.0 mDO saturated = 9.1 mg/LDO saturated = 9.1 mg/L Find the time and distance downstream at which the Find the time and distance downstream at which the

    oxygen deficit is a maximum?oxygen deficit is a maximum? Find the minimum value of DO?Find the minimum value of DO?

  • Streeter-Phelps Model Initial DeficitInitial DeficitDDoo = 9.1 = 9.1 7.6 = 1.5 mg/L7.6 = 1.5 mg/L Estimate the reaeration constantEstimate the reaeration constantEstimate the reaeration constantEstimate the reaeration constant

    [ ]( )( ) 12/3

    2120202/1

    2/3

    2/1

    2 day 14.0)0.3(025.1)/3.0(9.39.3

    ===

    m

    sm

    Hvk

  • Streeter-Phelps Model

    Calculate the time at which the maximum deficit Calculate the time at which the maximum deficit is reached, with tis reached, with tcc::

    kkDOkt o

    )(1ln1 122

    =

    mdaysdayssmvtxdays

    LkkkDO

    kk

    kkt

    cc

    o

    oc

    300,6967.2/400,86/3.067.2

    9.102.0)2.041.0(5.11

    2.041.0ln)2.041.0(

    1

    )(1ln11

    12

    1

    2

    12

    ===

    =

    =

    =

  • Streeter-Phelps Model

    The maximum DO deficit is:

    1 1=

    tkoc eLk

    kD

    mg/L 1.3

    e mg/L) 9.10(41.02.0 ))(2.67days(0.2day

    2

    1

    =

    =

    oc k


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