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    Enhanced Oil Recovery (EOR) Applications of CO2 Captured in Making

    Transportation Fuels Plus Electricity from Natural Gas and BiomassR.H. Williams

    CMI Carbon Capture Group

    Introduction Previous Capture Group research (Liu et al. 2010) showed that CCS

    systems coprocessing 1/3 biomass and 2/3 natural gas could provide FTL

    and coproduct electricity with ~ 10% of GHG emissions of fossil energy

    displaced at attractive costs under a C-mitigation policy (e.g., Fig. 1).

    Although a comprehensive US C-mitigation policy is not likely in the near

    term, there is an opportunity to take first steps along a path to

    coproduction of low-C transportation fuels and electricity by tying

    together three threads of industrial interest:

    Maximizing returns on new plants replacing coal (> 30 GW of coalpower to be retired by 2020)

    GTL as result of high oil/natural gas price ratio (Fig. 2)

    CO2 EOR (e.g., Energy Secretary Chu has asked the National Coal Council

    to prepare for him a report on opportunities to advance CCS

    technologies by using captured CO2 for EOR).

    Cai et al(2011)

    Findings Unlike NGCC plants, coproduction plants would be able to defend high

    design capacity factors in economic dispatch competition (see Fig. 5) and

    force down capacity factors of power-only competitors as their

    deployment on the electric grid increases.

    At high plant-gate CO2 prices PC-CCS retrofit is most profitable option,

    but at CO2 prices < $30/t, coproduction options are more profitablewith GBTL-OT-CCS-3.2% being most profitable, offering real IRRE >

    10%/y even for $0/t CO2 selling price (see Fig. 6).

    Coproduction plants could compete in remote EOR markets if an

    adequate trunk CO2 pipeline capacity were in place and in so doing

    would be more profitable investments than NGCC-V (see Fig. 6).

    Construction permitting should be easier/faster for rebuilds at

    brownfield sites where coal plants are being retired than at greenfield

    sites.

    There will soon be many brownfield sites in the Ohio River Valley (ORV)

    where > 40% of US coal capacity to be retired by 2020 capacity is located

    and also many shale plays (see Fig. 7).

    If both natural gas/biomass and coal/biomass coproduction plants were

    built at sites of old coal power plants in the ORV, they might pool their

    captured CO2 for transport via trunk CO2 pipelines to the EOR sites inGulf regionperhaps tying in to Denburys planned Rockport to Tinsley

    pipeline (see Fig. 8).

    Both coproduction plant designs (Tab. 1) could provide electricity with

    GHG emissions low enough to meet proposed EPA rules for new power

    plants if full fuel-cycle-wide GHG emissions were taken into account.

    The synthetic liquid fuels provided by these coproduction plants would

    meet GHG emissions requirement for Advanced Biofuels under RFS2

    Mandate, but would not qualify as advanced biofuels under the

    Mandate in its present form.

    CMI Annual Meeting, 17-18 April 2012

    References:

    Larson, E., R. Williams, and T. Kreutz, 2012: Energy, Environmental, and Economic (E3) Analysis of Design Concepts for the Co-Production of Fuels and Chemicals with Electricity via Co-Gasification of Coal and Biomass with CCS , Final Report to the National Energy Technology Laboratory for work completed under DOE Agreement DE-FE0005373, May (forthcoming)

    Liu, G., R. H. Williams, E. D. Larson and T. G. Kreutz. Design/Economics of Low -Carbon Power Generation from Natural Gas and Biomass with Synthetic Fuels Co- Production. 10th International Conference on Greenhouse Gas Technologies (GHGT-10), Amsterdam, Sept. 19-23, 2010.

    Autothermalreformer

    RefineryH2 prod.

    F-Trefining

    HCrecovery

    rawFTproduct

    Powerisland

    syncrude finished gasoline&diesel blendstocks

    fluegas

    netexportelectricity

    unconverted syngas

    +C1-C4FT gases

    lightends

    Naturalgas

    oxygensteam

    syngas

    Watergasshift

    CO

    2removal

    CO2 enrichedstreams, senttoupstreamCAP.

    steam

    FTsynthesis

    Chopping &Lockhopper

    Biomass

    oxygen steam

    CO2

    FBgasifier&Cyclone

    Dryash

    FilterCO2

    removal unit

    CO2 H2 make-up

    FIG. 1: Natural gas + biomass to FTL fuels + electricity in once-through

    system configuration with mild CO2 capture (OTonly naturallyconcentrated CO2 streams are captured); GTI fluidized bed gasifier for biomass

    (switchgrass); Autothermal reformer (ATR) simultaneously reforms natural gas

    into syngas and serves as tar cracker for tarry syngas from GTI biomass

    gasifier; Liquid phase FT synthesis with Co catalyst.

    FIG. 2: Crude oil-to-natural gas spot price ratio.

    TAB. 1: Some Coal-, NG-, Coal/Biomass-, and NG/Biomass-Based Energy Alternatives for Sites of Old Coal Power Plants (WO PC-V).

    The greenhouse gas emissions index (GHGI) is defined as the fuel cycle-wide GHG emissions for production and consumption divided by

    the GHG emissions of the fossil energy displaced, assumed to be electricity from a new supercritical coal plant and the equivalent crude

    oil-derived products.

    Technology

    Options

    106 t/y of

    biomass

    (% bio, HHV)

    Output capacities

    GHGICO2 stored, 10

    6 t/y

    (% feedstock C)

    Total plant

    cost, $106Transport fuel,

    B/D ge (%, LHV)

    Electricity

    MWeWO PC-V 0 (0) 0 543 1.19 0 0

    PC-CCS retrofit 0 (0) 0 398 0.23 3.47 (90) 752

    Rebuild Options

    NGCC-V 0 (0) 0 555 0.56 0 (0) 326

    NGCC-CCS 0 (0) 0 475 0.20 0.64 (90) 581

    GBTL-CCS-3.2% 0. 15 (3.2) 16,000 (58) 644 0.50 2.1 (46) 1598

    CBTG-CCS-5.0% 0.23 (5.0) 16,000 (74) 347 0.50 4.5 (64) 2550

    Using the economic framework shown in Fig. 4, both a minimum dispatch

    cost (MDC) analysis (Fig. 5) and an internal rate of return on equity (IRRE)

    analysis (Fig. 6) were carried out to compare these alternative options

    that would provide CO2 for EOR.

    -30

    -20

    -10

    0

    10

    20

    30

    40

    50

    60

    Crude oil

    products

    displaced

    C input

    to plant

    C output

    of plant

    Ceq emissions

    bycomponent

    Net Ceq

    emissions

    Net GHGemissions for GBTL-CCS-3.2%

    C extractedfrom atmospherevia photsynthesis

    Ceqcredit for electricityemissions (NGCC-Vrate)

    Ceqemissions upstream anddownstream of plant

    C inchar (tolandfill)

    C capturedas CO2 andstored

    C as CO2in fluegases

    C inFTL

    C innaturalgas toplant

    C inbiomass toplant

    Net GHGemissions for crudeoilproducts displaced

    FIG. 3: How a 50% reduction in GHG emissions for FTL is realized in a GBTL-CCS -3.2% plant.

    The above are the C and GHG balances for the GBTL-CCS-3.2%, for which the net kgCeq/GJ of FTL (5th bar) = 0.50 x [kgCeq/GJ of crude

    oil products displaced (1st bar)]. The plant was designed with enough biomass (3.2%) to reduce GHGI to 0.50. Assuming: (a) the latter

    is new supercritical coal plant emitting 229 kgCeq/MWh & (b) equal percentage reductions in emissions for FTL & electricity, theemissions credit for the electricity coproduct (in 3rd bar) = (0.50)*(0.203 MWhe/GJ FTL)*(229 kg Ceq/MWhe) = 23.2 kg Ceq per GJ FTL.

    0

    10

    20

    30

    40

    50

    0 10 20 30 40

    Plant-gate selling price of CO 2, $ per tonne

    NGCC-CCS

    NGCC-V

    GBTL-OT-CCS-3.2%,$90/B

    PC-CCS retrofit

    WOPC-V

    FIG. 5: Minimum Dispatch Cost (MDC), No C-Mitigation Policy.

    Systems with high MDCs cannot defend high design capacity factors

    in economic dispatch competition. During 2003-2009 (when gas

    prices were relatively high) the US average capacity factor (CF) for

    NGCC-V plants was 39%--much lower than the 85% design CF. More

    recently NGCC-V capacity factors have been higher because of lowergas prices. But if coproduction technologies become established in

    the market, they will be able to defend their high design capacity

    factors (90%) and force down capacity factors of competing power-

    only technologies on the grid as their market penetration increases.

    No curve is shown for CBTG-CCS-5.0% because its MDC is already$0/MWhe when the crude oil price is only $35/barrel.

    0

    3

    6

    9

    12

    15

    18

    0 10 20 30 40

    Plant-gate CO2 sellingprice,$/t

    NGCC-V(40% CF)

    NGCC-CCS (40% CF)

    PC-CCS retrofit

    GBTL-CCS-3.2%,$90/B

    CBTG-CCS-5.0%,$90/B

    FIG. 6: profitability of Near-Term Options for Providing Captured

    CO2 for EOR Applications, No C-Mitigation Policy. The PC-CCS retrofit

    is the most profitable option for high CO2

    selling prices highly

    competitive for nearby EOR opportunities. Coproduction options are

    more profitable for lower CO2 selling prices such systems could

    compete in remote EOR markets if adequate CO2pipelineinfrastructure were in place. Coproduction systems are more

    profitable than NGCC-V systems at all CO2

    selling prices. NGCC-CCS

    technology is not economically interesting.

    Although the CO2 capture rate

    for conventional GTL plant

    designs is small, substantial

    amounts of CO2 could be

    provided for EOR by plant

    designs for which electricity is a

    major coproduct (see Tab. 1).

    An analysis is presented for GBTL coproduction plants coprocessing 3.2%biomass (GBTL-CCS-3.2%) for which GHGI = 0.5 (Fig. 3) as rebuild option

    for old coal power plant sites that compete with post-combustion PC-CCS

    retrofit and coal/biomass coproduction coprocessing 5% biomass [CBTG-

    CCS-5.0% (Larson et al. 2012)]all capturing CO2 for EOR (Tab. 1).

    FIG. 4: Basis for Economic Calculations

    All costs in $2007 including construction costs as of that year

    (Owners cost)/[(total plant cost): 0.228 ( new construction); 0.202 (CCS retrofit)

    45/55 debt/equity ratio

    Real (inflation-corrected) cost of debt = 3.3%/year

    For endogenous determination of IRRE it is assumed that:

    Synfuels sold at refinery-gate price of equivalent crude oil-derived products

    Electricity sold at price = levelized cost of electricity for NGCC-V @ 40% CF

    These prices include value of GHG emissions based on GREET

    38% combined federal/state corporate income tax rate

    Property tax & insurance = 2% of TPC per year

    20-year economic life & physical life for plants

    Construction duration: 5 y (coproduction plants); 3 y (NGCC, PC-CCS retrofits)

    Assumed CF: 90% (coproduction plants); 85% (PC-CCS retrofits); 40% (NGCC)

    Assumed prices: $2.3/GJ (coal); $5/GJ (natural gas, biomass); $90/B (crude oil)

    FIG. 7: There are shale plays throughout much of the Ohio River Valley, for which announcements

    have been made that 14 GW of coal capacity will be retired by 2020. About the capacity

    represents 25 relatively large plants---the brownfield sites of which are candidates for rebuilds.

    FIG. 8: Denburys planned

    Rockport to Tinsley CO2 pipelineTAB. 2: Implications of alternative uses of 2.7 Quads/y of shale gas (enough to provide 0.5 MMB/D of FTL via GBTL-CCS-3.2%) GHG emissionsavoided are those for the equivalent crude oil products and average US coal plants in 2010 (for which GHG emissions = 1044 kgCO2eq/MWh).

    NGCC-V NGCC-CCS GBTL-CCS-3.2%

    Assumed capacity factor 40% 40%. 90%

    Generating Capacity supported, GWe 135 115 26

    Electricity generation , 106 MWhe/y

    (% of coal electricity in 2010)474 (26) 404 (22) 202 (11)

    Liquid fuels provided, 103 stream B/D

    FTL produced 0 0 500

    Incremental crude oil enabled by CO 2 EOR 0 1420 860

    GHG emissions avoided, 106 tonnes CO2eq

    /y 270 350 170

    Capital investment (TPC) required, $109 79 140 100

    GHGemissionsintensity,

    kgCeqperGJofFTL

    MDC,

    $perMWh

    Internalrateofreturn

    onequity,%peryear