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SKF 3413 POLLUTION CONTROL 1 Primary Wastewater Treatment
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  • SKF 3413 POLLUTION CONTROL

    1

    Primary Wastewater Treatment

  • Introduction

    Primary treatment Initial phase of wastewater treatment

    It uses physical treatment methods

    Removes settleable or floating solids only Goal : 60% of suspended solids in raw sewage

    35% of BOD5

    Ibm 2

    Primary treatment Initial phase of wastewater treatment

    It uses physical treatment methods

    Removes settleable or floating solids only Goal : 60% of suspended solids in raw sewage

    35% of BOD5

  • Raw Sewage

    Screening

    Grit Removal

    Pretreatment Primary Treatment

    Scope

    Ibm 3

    Grit Removal

    Equalization Basin

    Primary Settling

    Pump

    Figure 1 : Degrees of treatment

  • WasteWater

    Primary Treatment

    Ibm 4

    Screening Grit ChamberSedimentation tank

    WasteWater

  • Physical Unit OperationTreatmentProcess

    Physical Unit Operation Design

    Screening Bar Racks i) Manualii) Mechanical

    Fine Screen

    Comminutors

    Grit Removal Grit Chamber i) Velocity Controlledii) Aerated

    Ibm 5

    Grit Removal Grit Chamber i) Velocity Controlledii) Aerated

    Equalization Flow equalization i) In-line equalizationii) Side-line equalization

    Sedimentation(Solid-Liquidseparation)

    Clarifier i) Circular Solid Contactii) Parallel Inclined Plateiii) Tube settlers

    Flotation Dissolved-Air Flotation (DAF)

  • Definition:The process to remove large solids from the flow. unit operation that removes suspended matter from water.These may include natural and man-made trash (leaves,branches, roots, rocks, rags, and cans).

    Purpose of screening:To remove gross pollutants from the waste water stream

    Types of screening: Screens may be classified as course and fine screens,depending on the size of material removed

    SCREENING PROCESS

    Ibm 6

    Definition:The process to remove large solids from the flow. unit operation that removes suspended matter from water.These may include natural and man-made trash (leaves,branches, roots, rocks, rags, and cans).

    Purpose of screening:To remove gross pollutants from the waste water stream

    Types of screening: Screens may be classified as course and fine screens,depending on the size of material removed

  • Physical Unit Operation

    Bar Racks-Coarse Screening

    2 types : Manual Racks , Mechanical Racks

    Manual Racks Opening : 25mm 50 mm Channel Approach Velocity : 0.3-0.6 m/s

    Mechanical RacksOpening : 5 40 mm Channel Approach Velocity: 0.6-1.2 m/s

    Ibm 7

    Bar Racks-Coarse Screening

    2 types : Manual Racks , Mechanical Racks

    Manual Racks Opening : 25mm 50 mm Channel Approach Velocity : 0.3-0.6 m/s

    Mechanical RacksOpening : 5 40 mm Channel Approach Velocity: 0.6-1.2 m/s

  • Physical Unit Operation

    Fine Screen

    Used after the coarse screeningprocess Remove material that may createoperation and maintenance problems indownstream processes Consist of wedge-wire, perforated plateor closely a space bars with opening 1.5to 6.4 mmVelocity through the effective area : 0.4to 0.8 m/s.

    Ibm 8

    Fine Screen

    Used after the coarse screeningprocess Remove material that may createoperation and maintenance problems indownstream processes Consist of wedge-wire, perforated plateor closely a space bars with opening 1.5to 6.4 mmVelocity through the effective area : 0.4to 0.8 m/s.

  • Physical Unit Operation

    Comminutors

    Break up wastewater solid byrevolving cutting bars

    Placed downstream of grit chambers

    Ibm 9

    Comminutors

    Break up wastewater solid byrevolving cutting bars

    Placed downstream of grit chambers

  • Grit Chamber

    Grit : Inert Dense material such as sand, broken glass

    Purpose of Grit ChamberSlows down the flow to allow grit to fall out

    Consists of 2 basic types : Velocity controlled Aerated

    Ibm 10

    Grit : Inert Dense material such as sand, broken glass

    Purpose of Grit ChamberSlows down the flow to allow grit to fall out

    Consists of 2 basic types : Velocity controlled Aerated

  • Physical Unit Operation

    Velocity Controlled Grit Chambers(horizontal flow)

    Classical laws of sedimentationfor discrete, nonflocculatingparticles. (Type 1 sedimentation)

    Liquid velocity : 0.3 m/s

    Liquid velocity controlled byspecially designed weir.

    Ibm 11

    Velocity Controlled Grit Chambers(horizontal flow)

    Classical laws of sedimentationfor discrete, nonflocculatingparticles. (Type 1 sedimentation)

    Liquid velocity : 0.3 m/s

    Liquid velocity controlled byspecially designed weir.

  • Physical Unit OperationAerated Grit Chambers

    useful for the rapid separation of these inertparticles.

    Small, total volume based on 3-min retentionat maximum flow

    Diffused air create the mixing pattern withthe heavy, inert particles removed bycentrifugal action and friction against thetank walls.

    Floatable solids are removed in the aeratedgrit chamber.

    The settled grit is normally removed with acontinuous screw and buried in a landfill.

    Ibm 12

    useful for the rapid separation of these inertparticles.

    Small, total volume based on 3-min retentionat maximum flow

    Diffused air create the mixing pattern withthe heavy, inert particles removed bycentrifugal action and friction against thetank walls.

    Floatable solids are removed in the aeratedgrit chamber.

    The settled grit is normally removed with acontinuous screw and buried in a landfill.

  • Equalization

    Flow EqualizationIs used to overcome the operational problems caused by flow variations, toimprove the performance of the down stream processes and to reduce the sizeand cost of downstream treatment facilities

    Is the damping of flowrate variations so that a constant or nearly constantflowrate is achieved

    Achieved by constructing large basins that collect and store wastewater flowand from which waste water is pumped to treatment plant at a constant rate

    2 layouts of equalization : In-line equalization (ILE) ; Side-line equalization(SLE)

    Benefits biological treatment by providing steady flow and load

    Ibm 13

    Flow EqualizationIs used to overcome the operational problems caused by flow variations, toimprove the performance of the down stream processes and to reduce the sizeand cost of downstream treatment facilities

    Is the damping of flowrate variations so that a constant or nearly constantflowrate is achieved

    Achieved by constructing large basins that collect and store wastewater flowand from which waste water is pumped to treatment plant at a constant rate

    2 layouts of equalization : In-line equalization (ILE) ; Side-line equalization(SLE)

    Benefits biological treatment by providing steady flow and load

  • Rawwaste water

    1 2 3PrimarySedimentation4

    Screens Grit Removal

    EqualizationFlow control

    Figure 3 : In-line Equalization

    Flow Diagrams

    Ibm 14

    Rawwaste water

    1 2 3A

    3B

    PrimarySedimentation

    4

    Figure 4 : Side-line Equalization

  • A B

    Ibm 15

    CD

  • Sedimentation Tank

    Application: Removal of settleable solids Thickening of solids and biosolids

    Process: Allowing large amounts of suspended solids to settle

    at the bottom in the form of sludge Heavier solids settle by gravity Sludge are removed along with floating scum and

    grease Remove 25 to 50% of BOD5 ; 50 to 70% of

    suspended solids; 65% oil and grease

    Ibm 16

    Application: Removal of settleable solids Thickening of solids and biosolids

    Process: Allowing large amounts of suspended solids to settle

    at the bottom in the form of sludge Heavier solids settle by gravity Sludge are removed along with floating scum and

    grease Remove 25 to 50% of BOD5 ; 50 to 70% of

    suspended solids; 65% oil and grease

  • Physical Unit OperationA B

    Ibm 17

    C

    D

  • Physical Unit Operation

    Circular solid contact clarifierConfiguration:

    Used in larger tanks than was previously thecase particularly when the sedimentation tankis covered to facilitate odor removal

    Long sludge-holding times

    Efficiently used in chemical flocculantsuspensions

    Not suitable for biological suldges

    Ibm 18

    Circular solid contact clarifierConfiguration:

    Used in larger tanks than was previously thecase particularly when the sedimentation tankis covered to facilitate odor removal

    Long sludge-holding times

    Efficiently used in chemical flocculantsuspensions

    Not suitable for biological suldges

  • Physical Unit Operation

    Parallel inclined Plate CircularClarifierConfiguration:

    Large Surface AreaNo wind effectLaminar Flow

    Drawbacks :Long periods of Sludge deposits cause septiccondition

    Clogging of inner tube and channels

    Ibm 19

    Parallel inclined Plate CircularClarifierConfiguration:

    Large Surface AreaNo wind effectLaminar Flow

    Drawbacks :Long periods of Sludge deposits cause septiccondition

    Clogging of inner tube and channels

  • Physical Unit Operation

    Tube Settler RectangularClarifier

    Operation principle:

    Incoming flow enter tubes andflow upwardSolids settle inside the tubes andslide down into the hopper.

    Ibm 20

    Tube Settler RectangularClarifier

    Operation principle:

    Incoming flow enter tubes andflow upwardSolids settle inside the tubes andslide down into the hopper.

  • FlotationUnit operation used to separate solid or liquid particles from aliquid phase.

    Advantage : Flotation vs Sedimentation>>very small or light particles that settle slowly can be removedmore completely and in a shorter time

    Removal of finely divided suspended solids, particles withdensities close to that of water and also thickens biosolids.

    Chemicals are commonly used to aid the flotation process wherethe function is to create a surface or a structure that can easilyabsorb or entrap air bubbles (i.e aluminium and ferric salts,activated silica)

    Ibm 21

    Unit operation used to separate solid or liquid particles from aliquid phase.

    Advantage : Flotation vs Sedimentation>>very small or light particles that settle slowly can be removedmore completely and in a shorter time

    Removal of finely divided suspended solids, particles withdensities close to that of water and also thickens biosolids.

    Chemicals are commonly used to aid the flotation process wherethe function is to create a surface or a structure that can easilyabsorb or entrap air bubbles (i.e aluminium and ferric salts,activated silica)

  • Physical Unit Operation

    Dissolved Air Flotation (DAF)

    Operation Principle:

    Dissolving air in the water or wastewaterunder pressure and then releasing the airat atmospheric pressure in a flotation tankor basin.

    The released air forms tiny bubbles whichadhere to the suspended matter causingthe suspended matter to float to thesurface of the water where it may then beremoved by a skimming device

    Ibm 22

    Dissolved Air Flotation (DAF)

    Operation Principle:

    Dissolving air in the water or wastewaterunder pressure and then releasing the airat atmospheric pressure in a flotation tankor basin.

    The released air forms tiny bubbles whichadhere to the suspended matter causingthe suspended matter to float to thesurface of the water where it may then beremoved by a skimming device

  • Conclusion

    Primary treatment is generally understood as theset of operations performed to remove floatableand settling solids

    Other benefits of primary settling includeequalization of side stream flows and removalof the biochemical oxygen demand (BOD)associated with settleable solids.

    In primary treatment only physical operationssuch as screening, sedimentation and flotationare used.

    Primary treatment is generally understood as theset of operations performed to remove floatableand settling solids

    Other benefits of primary settling includeequalization of side stream flows and removalof the biochemical oxygen demand (BOD)associated with settleable solids.

    In primary treatment only physical operationssuch as screening, sedimentation and flotationare used.


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