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    D e p a r

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    Bauhaus-Universit Weimar

    D i p l . - I n g .

    S t e n

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    Sludge Settling Processes in SBR-SewageTreatment Plants

    According to theBiocos-Method

    Dipl.- Ing. Sten Meusel

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    Forecast

    Peculiaritiesof the sludge sedimentation

    andproblematic operating conditions

    observed inthree-phase-Biocos-plants

    Peculiaritiesof the sludge sedimentation

    andproblematic operating conditions

    observed in

    three-phase-Biocos-plants

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    Outline

    1. Motivation of Investigation

    2. Methods and Material

    3. Results4. Summary

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    1. Motivation of Investigation

    Few availableempirical data

    about sludgesettling processes

    in Biocos-plants

    Few availableempirical data

    about sludgesettling processes

    in Biocos-plants

    Improvement of the Biocos-method

    concerning theoperatingefficiency

    Improvement of the Biocos-method

    concerning theoperatingefficiency

    Bauhaus-University

    Weimar

    Bauhaus-University

    Weimar

    Company of Biocos-plantconstructions

    Company of Biocos-plantconstructions

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    2. Methods and Material

    SU 2 SU 1

    Biological reactor

    WWTP Buchbach(Capacity 1,200 PE)

    WWTP Buchbach(Capacity 1,200 PE)

    Q in= 0...5 L/s or 10 L/s

    Design MLSS B = 5 g/L

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    M e u s e l Q out

    2. Methods and Material

    Mixing phase U (15 min)Mixing phase U (15 min)

    Q in

    Longitudinal Section

    Plan View

    B SU 1

    B

    SU 1

    SU 2

    Q in

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    M e u s e l Q out

    2. Methods and Material

    Settling phase V (45 min)Settling phase V (45 min)

    Q in

    Longitudinal Section

    Plan View

    B SU 1

    B

    SU 1

    SU 2

    Q in

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    Qout

    Qout

    2. Methods and Material

    Discharge phase A (60 min)Discharge phase A (60 min)

    Q in

    Longitudinal Section

    Plan View

    B SU 1

    B

    SU 1

    SU 2

    Q in

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    2. Methods and Material

    Focal points of the investigations in the SU-reactor:

    Definition of the sludge level courses Definition of the solid distribution

    Measuring instrument:

    Infrared light turbidity sensor ( CUC 101, Endress+ Hauser) Total solids (TS) in g/L

    Arrangement of measurement points (Units in m):

    Length = 8.0 m

    Width = 3.5 mMax water depth = 4.5 m

    l

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    3. Results

    Sludge levels during the Settling phase V:

    Time during V-phase [min]

    Calculated sludge settling rates (SSR):

    0

    0,5

    1

    1,5

    2

    2,5

    3

    3,5

    4

    250 300 350 400 450 500 550 600Vergleichsschlammvolumen VSV [ml/l]

    A b s e t z g e s c h w i n d i g k e i t [ m / h ]

    Merkel (1971)

    Resch (1981)

    ATV-M 210 (1997)

    Kayser (1995)

    Absetzgeschwindigkeiten der Profillufe

    Absetzgeschwindigkeiten der manuellenMessungen

    250 300 350 400 450 500 550 600Sludge volume SV30(SU) [mL/L]

    Merkel (1971)

    Resch (1981)

    ATV-M 210 (1997)

    Kayser (1995)

    Measured settlingrates

    MLSSSU

    = 5.54 g/L SV 30,SU = 510 mL/L

    MLSS SU = 5.04 g/L SV 30,SU = 440 mL/L

    MLSS SU = 4.79 g/L SV 30,SU = 410 mL/L

    MLSS SU = 4.05 g/L SV 30,SU = 370 mL/L

    0 5 10 15 20 25 30 35 40 45

    43.5

    3

    2.52

    1.51

    0.50

    S l u d g e s e

    t t l i n g r a

    t e

    [ m / h ]

    0

    0.2

    0.4

    0.6

    0.8

    1.0

    1.2

    1.4 D e p

    t h o

    f s l u d g e

    l e v e

    l [ m

    ]

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    3 R lt

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    3. Results

    Longitudinal profiles of the solid matter distribution in the SU-reactor

    V-phase(after 45 min)

    V-phase(after 45 min) MLSS SU = 5.3 g/LMLSS SU = 4.1 g/L

    0 0.5 1.51 2.52 3.53 4.54 5.55 6.56 7.57 8

    52 8

    1

    4.5

    4

    3

    3.5

    2.5

    1.5

    2

    0.5

    0

    Klarwasserzone

    TS= 0

    Absetzzone

    1 2 3 4 5 5.25 6

    Eindickzone

    7 8 9 1110 12 13 g/l

    0

    1

    2

    3

    4

    0 1 2 3 4 5 6 7 8[m]

    Clear water zone

    Separationzone

    Compressionzone

    TS = 0 1 2 3 4 5 5.25 6 7 8 9 10 11 12 13 [g/L]

    40 210.5 1.5 32.5 3.5 54.5 5.5 6.56 7.57 8

    2

    2.5

    4.5

    4

    3

    3.5

    1

    2

    1.5

    0.5

    0

    5 9

    TS= 0 1 32 4

    Klarwasserzone Absetzzone Eindickzone

    75.285 6 8 9 10 13 g/l1211

    0

    1

    2

    3

    4

    0 1 2 3 4 5 6 7 8[m]

    Clear water zone

    Separationzone

    Compressionzone

    TS = 0 1 2 3 4 5 5.28 6 7 8 9 10 11 12 13 [g/

    Break pointconcentration

    Break pointconcentration

    3 R lt

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    3. Results

    A-phase(after 55 min)

    A-phase(after 55 min) MLSS SU = 5.3 g/LMLSS SU = 4.1 g/L

    0 0.5 1 1.5 2 2.5 3 3.5 4 4.5 5 5.5 6 6.5 7

    2 5

    4

    7.5 8

    4.5

    2.5

    3.5

    3

    2

    1.5

    8

    0.5

    1

    0

    10 0.5

    2

    87.576.565.554.543.532 2.51.5

    0

    0.5

    1

    2

    2.5

    1.5

    3

    4

    3.5

    4.5

    5 9

    Klarwasserzone

    TS= 0

    Absetzzone

    1 2 3 4 5 5.25 6

    Eindickzone

    7 8 9 1110 12 13 g/l

    0

    1

    2

    3

    4

    0 1 2 3 4 5 6 7 8[m]Clear

    water zone

    Separationzone

    Compressionzone

    TS = 0 1 2 3 4 5 5.25 6 7 8 9 10 11 12 13 [g/L]TS= 0 1 32 4

    Klarwasserzone Absetzzone Eindickzone

    75.285 6 8 9 10 13 g/l1211

    0 1 2 3 4 5 6 7 8[m]Clear

    water zone

    Separationzone

    Compressionzone

    TS = 0 1 2 3 4 5 5.28 6 7 8 9 10 11 12 13 [g/L

    0

    1

    2

    3

    4

    3 Results

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    3. Results

    Concentration interchange of the Mixing phase U

    Problems of concentration

    equalisation measured

    (MLSS SU > MLSS B)

    Problems of concentration

    equalisation measured

    (MLSS SU > MLSS B)

    B S

    U

    Internal sludgecirculation in the SU-

    reactor

    Internal sludge

    circulation in the SU-reactor

    Interchanging rate of the recirculation pump

    = 1.2 SU-reactor content

    MLSS B 4 g/L

    Difference atboth inflow

    types

    MLSS B 5 g/L

    Difference onlyduring storm

    water inflow

    3 Results

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    3. Results

    Four-phase-Biocos-methodMixing phase + Sludge recycle phase

    Four-phase-Biocos-method

    Mixing phase + Sludge recycle phase

    Q out

    Q in

    Longitudinal Section

    Plan View

    B SU 1

    B

    SU 1

    SU 2

    Q in

    Sludge recycling pumpSludge recycling pump

    4 Summary

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    4. Summary

    Results of investigation:Results of investigation:

    2. During the Discharge phases:Sludge levels depending on the difference between

    sludge settling rate and surface overflow rateSolid matter distribution comparable to layer formations insecondary clarifiers with vertical flow

    1. During the Settling phases: Almost linear sludge level decreases depending on sludge volum Settling processes analogue to well-known hydraulically uninterrupted settling processes

    Intention of investigation:Intention of investigation:

    Determination of solid matter distribution and sludge levelduring the Settling and Discharge phases

    3. Problematic concentration interchange during theCirculation phases Four-phase-Biocos-method

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    Backup slide 1

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    Backup slide 1

    Measuring instrumentMeasuring instrument

    Microprocessor with display

    Stepper motor

    Cable drum

    Turbidity sensor

    Optoelectronical measuring system CUC 101 (Endress + Hauser)

    Sensor in stop-positionSensor in stop-position

    Endress + Hauser 2004

    Backup slide 2

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    Backup slide 2

    Measurement arrangementMeasurement arrangement

    Measuring No. 1 2 3 4 5 6 7 8 9

    Phase V V V V A A A A A

    Time after phase start 8 min 19 min 30 min 40 min 12 min 23 min 34 min 44 min 55 min

    Defined measuring intervals of the test series

    Measuring platforms with the 10 measurement points

    Backup slide 3

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    ac up s de 3

    Dimensioning of the Biocos reactorsDimensioning of the Biocos reactors

    Biological reactor Biological reactor

    solids suspended liquor mixed Designage sludge Designproduction SludgeloadingBOD Volume 5

    SU-reactor SU-reactor

    solidssuspendedliquor MixedindexvolumeSludgeL/m/h)(675rateloadingsurfacevolumeSludge

    rate settlingSludge

    rate settlingSludgeinflowwater Storm

    areaSurface