Cervercia India Puerto Rico Presentacion- WWTP Upgrade L1

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    Wastewater Treatment Plant UpgradeProject (WWTP)

    Marlon CabreraEngineering Department

    Cervecera de Puerto RicoMayaguez, PR

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    Introduction

     A common challenge for breweries is meeting currentwastewater discharge standards while accommodatinggrowth and anticipating more stringent discharge

    regulations in the future. Cervecera de Puerto Ricowastewater treatment system had been in operation for along time, but years of service and increased hydraulic andorganic loadings had made it difficult to meet treatmentobjectives.

    For years Cervecera de Puerto Rico wastewater treatmentplant was affecting the image of the company and hadbecome a priority for the future of the company.

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    Potential Issues

    • Regulatory Compliance of Waste Water Discharge

    • Possible surcharges

    • Controls were mostly manual, there were no instrumentation automated monitoringparameters of waste water treatment process

    • Operation of Return Activated Sludge Systems (RAS) was inconsistent due a to pastretrofits and obsolete equipment

    • Operation and maintenance  of the treatment systems rotating biological contactors hadbecome a very high total operational costs

    • Increased hydraulic and organic loadings

    • Bad odor generation at the treatment plant

    • Bad ima e of the com an

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    Before Process Diagram of WWTP 

    Pista-Grit

    Equalization TankDigester/

    Thickener  

    Clarifier

    Pump #1

    Pump #2

    Blockeddischargeconnectionsto/from reactor

    Pressed if

    needed

    Reactor

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    Previous Rotating Biological

    Contactors

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    Previous Rotating Biological

    Contactors

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    Previous Clarifier

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      Legal Limits and Requirement of

    Samples Applied Load

    PARAMETERS DOWNLOAD LIMIT

    BOD (mg/L) 250

    TSS (mg/L) 250

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    Before - Graph of BOD 

    0

    200

    400

    600

    800

    1000

    1200

    1400

    1600

       B   O   D    (   g    /   m    l    )

    Month/Year

    Biochemical Oxygen Demand

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    Before - Graph of TSS 

    0

    500

    1000

    1500

    2000

    2500

       T   S   S    (   g    /   m    l    )

    Month/Year

    Total Suspended Solids

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    Challenges

    • Regulatory compliance with the permit.

    • Reduce the environmental footprint of the plant

    • Cost effective technologies

    • Limited budget of 1.3M

    • Space construction limited

    • Withstand large changes in demand while maintaining efficient

    • Reduce odors

    • Make changes without stopping operation

    • Reduce total operating costs

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    CERVECERA DE PUERTO RICO PILOT

    study MOVING BED BIOREACTOR

    (MBBR) TECHNOLOGY

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    CERVECERA DE PUERTO RICOWWTP MBBR PROJECT

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     Paramecium Vorticella

    EpistilysVorticella

    CERVECERA DE PUERTO RICO WWTP MBBR PROJECT

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    0.00

    500.00

    1000.00

    1500.00

    2000.00

    2500.00

    3000.00

    3500.00

    4000.00

    3578.00

    1193.00

    186.00 29.30 250.00

       S   O   L   U   B   L   E   B   O   D    (   P   P   M    )

    SOLUBLE BOD 10/23/2009

    INFLUENTE SOLUBLE BOD WWTP REACTOR SOLUBLE BOD MBBR #1

    SOLUBLE BOD MBBR #2 PRASA BOD PERMIT LIMIT

    CERVECERA DE PUERTO RICOWWTP MBBR PROJECT

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    0.00%

    10.00%

    20.00%

    30.00%

    40.00%

    50.00%

    60.00%

    70.00%

    80.00%

    90.00%

    100.00%

    61.08%

    93.93%99.04%

    SOLUBLE BOD REMOVAL 10/23/2009

    BOD REMOVAL % WWTP REACTOR BOD REMOVAL % MBBR #1

    BOD REMOVAL % MBBR #2

    CERVECERA DE PUERTO RICO WWTPMBBR PROJECT

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      Solution: Upgrading the WWTP

    The Engineering Department along with EH&S evaluateddifferent treatment alternatives to determine the viability ofupgrading the existing facilities to achieve permitparameters.

    • Moving Bed Biofilm Reactor (MBBR)

    • Tank Dissolved Air Flotation (DAF), system without airsaturation

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    MBBR Design Basis

    PARAMETER  UNITS  INFLUENT  EFFLUENT 

    Flow MGD 0.15 0.15

    BOD5  (Soluble) MG/L 1,800

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    Project Scope

    Tasks Original Scope Currently AchievedReactor Tank Retrofit X X

    Blowers Replacement X X

    DAF Installation X X

     Acid Dosing Station Automation X X

    Caustic Soda Station Automation X X

    Caustic Soda Receiving Station Automation X

    pH/Temp Monitoring EQ Tank X X

    pH/Temp/DO Monitoring Reactor Tank X X

    Influent Flow Metering X X

    Influent Temperature Monitoring X

    Central process overview X X

    Tank Levels X X

    Belt Press automation X

    Electrical Utilities X

     Air Utilities X

    Water Utilities X

    Pads/Dikes/Civil Work X

    Instrumentation and Integration X X

     Aesthetical Improvement X

    Waste Water Lift Station Upgrade XNew Laboratory Furniture X X

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    Project Budget

    • Project Budget $1,394,036

    • Discharge Overcharges $98,069

    • Negotiated PRASA Limits

    • BOD - 5,633 mg/L

    • TSS - 2,628 mg/L

    • Currently consumed $1,358,641

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     Actual Process Diagram of WWTP

    Belt Filter

    Press &

    Container

    Moving Bed

    Biofilm

    Bioreactor

    (315,000 gals)

    Digester

    89,000 gals

    Screens

    DAF

    UtilitiesBrew HouseCold BlockPacking Lines

    PRASA

    Equalization

    Tank

    292,000 gals

    Lift Station

    X X X

    X XBlowers

    Blowers

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    Moving Bed Biofilm Reactor

    (MBBR)

    •  A stand-alone biological treatment system with no needfor media backwashing

    • Wastewater treatment plants of this type operate asfixed-film processes without activated sludge recyclebetween the bioreactor and clarification units

    •  Aeration supplied provides oxygen, essential formicrobial growth, and the energy required to dispersethe carriers completely throughout the system

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      Moving Bed Biofilm Reactor(MBBR)

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    MBBR System

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    Moving Bed Biofilm Reactor

    (MBBR)

    Process uses 25 mm-diameter cylindrical plastic carriersthat provides environments in which bacteria andprotozoa can grow effectively.

    M i B d Bi fil R t

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    Moving Bed Biofilm Reactor

    (MBBR)

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    Dissolved Air Flotation

    Operation (DAF) 

    Separates and optimizes solids prior to dewatering

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    Dissolved Air Flotation

    Operation (DAF)

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    Dissolved Air Flotation

    Operation (DAF) 

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    WWTP Retrofit

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    WWTP Retrofit

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    WWTP Retrofit

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    WWTP Retrofit

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    WWTP Retrofit

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     Belt Press

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    Now - Graph of TSS 

       2   0

       1   6   0   0

       1   0   2

       0

       2   6   0

       2   3   0

       2   4   0

       2   2   0

       2   0   0

       1   5   0

       1   4   0

       1   1   0   1   5   0

       2   7   0

       2   8   0

       1   4   3

       1   3   5

       1   2   1

       1   1   0   9   0   3   0   3   0   2   0

       1   5   2   0   1   5   1   20

    250

    500

    750

    1000

    1250

    1500

    1750

    2000

    2250

    2500

       J  a  n  -   0   8

       M  a  r  -   0   8

       M  a  y  -   0   8

       J  u   l  -   0   8

       S  e  p  -   0   8

       N  o  v  -   0   8

       J  a  n  -   0   9

       M  a  r  -   0   9

       M  a  y  -   0   9

       J  u   l  -   0   9

       S  e  p  -   0   9

       N  o  v  -   0   9

       J  a  n  -   1   0

       M  a  r  -   1   0

       M  a  y  -   1   0

       J  u   l  -   1   0

       S  e  p  -   1   0

       N  o  v  -   1   0

       J  a  n  -   1   1

       M  a  r  -   1   1

       M  a  y  -   1   1

       J  u   l  -   1   1

       S  e  p  -   1   1

       N  o  v  -   1   1

       J  a  n  -   1   2

       M  a  r  -   1   2

       M  a  y  -   1   2

       J  u   l  -   1   2

       T   S   S   (  g   /  m   l   )

    Month/Year

    Total Suspended Solids Efficiency

     Actual TSS

    Before TSS

    Limit

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    Now - Graph of BOD 

       1   0 .   0

       0

       7   0

       0 .   0

       0

       1   3   3 .   0

       0

       1   1   1 .   0

       0

       1   9   3 .   0

       0

       1   2   8 .   0

       0

       1   0   1 .   0

       0

       1   2   1 .   0

       0

       1   9   3 .   0

       0

       1   3   3 .   0

       0

       4   2 .   0

       0

       2   4 .   0

       0

       2   4 .   0

       0

       4   0 .   0

       0

       3   0 .   0

       0

       1   8 .   0

       0

       2   1 .   0

       0

       1   4 .   0

       0

       1   1 .   0

       0

       6 .   0

       0

       8 .   0

       0

       7 .   0

       0

       1   0 .   0

       0

       7 .   0

       0

       8 .   0

       0

       8 .   0

       0

    -200

    0

    200

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    800

    1000

    1200

    1400

    1600

       J  a  n  -   0   8

       M  a  r  -   0   8

       M  a  y  -   0   8

       J  u   l  -   0   8

       S  e  p  -   0   8

       N  o  v  -   0   8

       J  a  n  -   0   9

       M  a  r  -   0   9

       M  a  y  -   0   9

       J  u   l  -   0   9

       S  e  p  -   0   9

       N  o  v  -   0   9

       J  a  n  -   1   0

       M  a  r  -   1   0

       M  a  y  -   1   0

       J  u   l  -   1   0

       S  e  p  -   1   0

       N  o  v  -   1   0

       J  a  n  -   1   1

       M  a  r  -   1   1

       M  a  y  -   1   1

       J  u   l  -   1   1

       S  e  p  -   1   1

       N  o  v  -   1   1

       J  a  n  -   1   2

       M  a  r  -   1   2

       M  a  y  -   1   2

       J  u   l  -   1   2

       B   O   D    (   g    /   m    l    )

    Month/Year

     Actual BOD

    Before BOD

    Limit

    Biochemical Oxygen Demand Removal Efficiency 

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    Summary Savings

    • Maintenance Costs 70%

    • Chemicals 50%

    • Generation of H2O

    • Power Cost 35%

    • Odor reduction

    • Regulatory compliance without overcharges 100%