Benko - IPEC 2008 - Final

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    Use of Ceramic Membranes forProduced Water Treatment

    Katie Benko, Bureau of Reclamation and Colorado School of Mines

    Jrg Drewes, Colorado School of Mines

    Pei Xu, Colorado School of Mines

    Tzahi Cath, Colorado School of Mines

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    Outline

    Why use ceramic membranes for producedwater treatment

    Benefits and limitations of ceramicmembranes

    Comparison of ceramic and polymericmembranes

    Ceramic membrane manufacturers and

    products

    Use of ceramic membranes for producedwater

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    Treatment of Produced Water

    Livestock & CropIrrigation

    Surface DischargeDomestic Home Use

    Degree of treatment depends on raw waterquality and desired end use

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    Pretreatment Technologies Current approaches:

    Dissolved air flotation

    Media filtration

    Polymeric membranes

    Novel approaches: Ceramic microfiltration and ultrafiltration

    Membrane distillation(HydroflowTM)

    Hydroflow Degremont

    CeraMem

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    Treatment Design Criteria

    Geographical issues

    Minimal Maintenance Easy to operate

    Robust and reliable

    Changing water quantity andquality

    Flexible

    Modular

    Cost

    Minimal pretreatment

    Low chemical and energy

    demand

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    Benefits High mechanical strength

    High chemical compatibility

    High flux (up to 300 gfd)

    Long operational life Thermal stability

    Potentially lower life-cycle cost

    Potential limitations High capital cost

    Benefits and Limitations of CeramicMembranes

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    Membrane Filtration Market

    0%

    20%

    40%

    60%

    80%

    100%

    2001 2005 2010Polymeric Ceramic Other

    Data from Pall Corporation

    The ceramic membranemarket share isexpected to grow infuture years!

    Advances in materials,configuration, andoperational experiencewill make ceramicmembranes more widelyused.

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    Membrane Transport Properties

    Pure Water

    Permeance(L/m2/hr/Pa)

    MembraneResistance (1/m)

    Ceramic UF 1.3 0.1 2.2 x 105 0.2 x 105

    Polymeric UF 0.87 0.08 2.3 x 106 0.2 x 106

    Ceramic membranes have significantly higher permeance

    and lower membrane resistance than polymeric

    membranes

    Ceramic membranes have a lower membrane resistance,

    therefore require a lower pressure to produced the same

    volume of water

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    Cost Comparison

    Material Cost($/ft2)

    Material Cost

    ($/vol produced)

    Ceramic UF 180 60

    Polymeric UF 40 20

    Fewer ceramic membranes are required to treat the same

    volume of water Ceramic membranes have higher capital cost but longer

    lifespan

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    Membrane and

    Support(100x 300x)

    Support

    (1000 3000x)

    MembraneSurface (5000x)

    Ceramic UF

    Membrane

    Polymeric UF

    MembraneSpintekwww.spintek.com

    SEM: Ceramic and Polymeric

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    Ceramic Membrane Manufacturers*ProductLine(s)

    FiltrationRange

    SupportMaterials

    MembraneMaterials

    ChannelConfiguration

    PallMembralox

    Schumasiv

    5nm to

    0.2 mAl2O3

    Al2O3 (MF)

    ZrO2 andTiO2 (UF)

    Hexagonal

    and round

    Corning CerCor5nm to

    0.2 m

    Mullite

    (3Al2

    O3

    2

    SiO2)

    ZrO2 (MF)

    TiO2 (UF)

    Square and

    round

    TAMICeram

    Inside

    0.02 m

    to 1.4mATZ

    ZrO2 (MF)

    TiO2 (UF)Flower shaped

    Atech Atech 0.01 mto 1.2 m Al2O3

    Al2O3 (MF)

    ZrO2 andTiO2 (UF)

    Single ormultiple round

    Orelis Kerasep5 kDa to

    0.8 mAl2O3

    ZrO2 andTiO2

    Single or

    multiple round

    *Not a complete list

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    Contaminant Removal Capability What they will remove

    Suspended solids

    Oil and grease

    Organic carbon (to some

    degree) Metal oxides

    What they will NOT

    remove Dissolved ions Dissolved organics

    Feed Reject Filtrate

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    Ceramic Membrane System Operation

    Dead-end versus cross-flow filtration

    Elizabeth L. Brainerd, Nature 412, 387-388(26 July 2001)

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    Important Operating Parameters

    Flux: volumetric flow rate of product water per area of

    membrane Trans-membrane pressure: average of feed and reject

    pressure minus filtrate pressure

    Cross-flow velocity: Velocity of water moving throughmembrane channel

    Backwash or backpulse: flow of water from the filtratesize to the feed size, rather than the feed side to thefiltrate

    In-line coagulation: dose of coagulant in the feed streamwith no flocculation or settling; formation of pin-sized

    floccs that are more easily rejected by the membraneand increase the rejection of dissolved organics

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    0

    50

    100

    150

    200

    250

    300

    350

    400

    0 0.5 1 1.5 2 2.5 3 3.5 4 4.5 5

    Time (hr)

    TemperatureCorrectedFlux

    (gfd)

    CBM Produced Water Raton Basin

    Membrane Specs: Feed Water: Operating Conditions:85 channels

    cylindrical channels

    0.01 um pore size

    TDS = 2300 mg/L

    TOC = 0.27 mg/L

    TSS = 0.7 mg/L

    Total Fe > 0.3 mg/L

    SDI = 18

    TMP = 60 psi

    Crossflow = 0.46 ft/s

    Full recycle

    Backwash every 15 min

    No coagulant

    Feed water changed

    Filtrate SDI = 1.8

    12.5% flux decline over 5 hours

    System reached steady state

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    Full-Scale Ceramic MembraneTreatment of Produced Water

    Ceramic membranes used to removeorganic contaminants approximately 1 to 3um in size and as pretreatment to RO

    System configuration: cross-flow velocity = 10 fps backpulse every 90s

    chemical cleaning every 24 hrs

    Filtrate SDI < 1, suitable as pretreatmentfor RO

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    Summary Ceramic membranes are a viable technology for

    produced water treatment. There are a number of different ceramic membrane

    manufacturers with a wide variety of products tochoose from.

    Ceramic membranes can remove silt, particulates, oiland grease, metal oxides, and some dissolved organicmatter.

    Operational conditions of ceramic membranes still

    need to be optimized for different water types. Ceramic membranes have worked effectively at the

    laboratory scale and full scale for treatment ofproduced water.

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    Acknowledgements Bureau of Reclamation

    Science andTechnology Program

    NWRI ResearchFellowship

    Corning Incorporated

    George Kellogg

    Andy Pierce

    Bureau of Reclamation Erik Jorgensen

    Dan Gonzales

    Tom Bunnelle

    AQWATEC

    Ryan Decker Katharine Dahm

    Eric Dickenson

    Dean Heil

    JT Teerlink

    Research Partnership toSecure Energy forAmerica

    Dave Stewart, Stewart

    Environmental

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    Contacts

    Katie Benko, Bureau of [email protected](303) 931-8396

    Jrg Drewes, Colorado School of [email protected](303) 273-3401