GREEN ENERGY: PRODUCTION OF ALCOHOLS FROM SWITCHGRASS Group Alpha Greg Dicosola Tim O’Brien Tim Bannon Hasseb Quadri Catalina Mogollon OUTLINE PFD Gasification Gas Clean Up Alcohol Synthesis Waste Streams Basic Cost Estimation PFD 19 TO WASTE PFD 2 HEAT RECOVERY 17 5 13 16 CYCLONE 4 10 CYCLONE 3 11 4 TCCB-TAR CATALYTIC CRACKER B TCCA-TAR CATALYTIC CRACKER A CYCLONE 1 30 DRIED FROM PFD 2 BIOMASS CYCLONE 2 8 6 GASIFIER 12 9 SHREDDER/ HOPPER 3 COMBUSTER 15 TO BIOMASS ASH TO PFD 2 DRYER 14 AIR HEAT EXCHANGER/ SUPERHEATER 1 OSBL FLOW VALVE TO PFD 4 FIC 7 FIC 2 1 STEAM FROM FROM PFD 3 SUPERHEATER Page 1 PFD: Gasifier, Combuster, and Tar removal PIC 23 STEAM TO PFD 4 SYN GAS FROM 19 FROM PFD 1 TAR REMOVAL 24 25 DI WATER OSBL 29 WASTE HEAT BOILER TO CO2/H2S TO PFD 3 ABSORBER 28 CWS PIC 20 FIC 21 INITIAL COMPRESSOR WATER QUENCH 27 GAS /WATER SEPARATOR 22 LIC 26 MOISTURE 31 WASTE WATER OSBL WET BIOMASS OSBL 30 DRIED BIOMASS TO PFD 1 TO FEEDER CONVEYER/ DRYER PIC TO FLARE OSBL FLUE GAS FROM PFD 1 15 32 Page 2 PFD: Waste heat recovery and Biomass Drying 42 METHANOL RECYCLE FROM PFD 4 PIC 50 STEAM TO PFD 4 43 LIC 41 MIXED ALCOHOL REACTOR (boiling water reactor) CWS 49 BOILER OSBL FEED WATER EXCHANGE TO FROM PFD 4 TIC REACTOR EFFLUENT 47 40 44 PIC 48 HEAT EXCHANGER 2/ STEAM SUPERHEATER 45 39 COMPRESSOR EXCHANGE FROM TO PFD 4 REACTOR EFFLUENT 33 PIC 46 51 55 GAS TO VENT OSBL CO2 /H2S ABSORBER HP GAS/ LIQUID SEPARATOR 38 PIC LIC 29 PIC FROM FROM PFD 2 CO2 TO VENT LIC COMPRESSOR 56 CWS 53 LIC WATER 34 52 LP GAS/ LIQUID SEPARATOR OSBL 35 36 LIC AMINE HEAT EXCHANGER MIXED ALCOHOL TO PFD 4 54 AMINE STRIPPER 37 RESET FIC XY/XV SOLVENT STEAM LIC OSBL MAKE-UP Page 3 PFD: CO2, H2S removal and Alcohol synthesis TO FRACTIONATION 47 EXCHANGE FROM FROM PFD 3 REACTOR EFFLUENT POWER TO RELAY FOR PLANT OPERATION 61 OSBL (ADDITIONAL POWER TO BE SOLD) STEAM FROM REACTOR 50 57 58 59 FROM PFD 3 HEAT EXCHANGER 2/ STEAM SUPERHEATER STEAM FROM 23 FROM PFD 2 WASTE HEAT BOILER 48 EXCHANGE TO TO PFD 3 REACTOR EFFLUENT 60 WATER TO OSBL FLOW WASTE HEAT BOILER AND/OR REACTOR CWS FROM PFD 1 CONTROLLER PIC 1 STEAM TO GASIFIER 64 METHANOL TO TO PFD 1 TO PFD 3 REACTOR 62 LP GAS/ LIQUID SEPARATOR LIC 65 WATER TO CLEAN-UP OSBL WATER/METHANOL FRACTIONATION FROM MIXED ALCOHOL STREAM MIXED ALCOHOL FROM PFD 3 FROM SEPARATOR 53 FIC 63 MIXED ALCOHOL OSBL PRODUCT Page 4 PFD: Steam superheating, Power generation, and Product fractionation GASIFICATION THE SILVAGAS PROCESS1 • Twin Fluidized Bed Process • Steam Gasification • Endothermic gasification in the gasifier (Left) • Exothermic combustion in the combustor (Right) • Sand recycled to transfer heat ADVANTAGES OF THE SILVAGAS PROCESS • Designed for biomass gasification (adaptable to forest waste, MSW, agricultural waste, and energy crops). • High throughput—up to 3000 lb/hr-ft2 (compared to 100 lb/hr-ft2 of comparable gasification processes). • Syngas composition remains same regardless of changes in feedstock moisture levels (proven within 10-50%3) • No pure oxygen required – steam gasification.2 • Short residence times of a few minutes.3 GASIFIER MATERIAL BALANCE • Choose Basis—used 133,333 acres/year at 11.5 tons/acre in Alabama4 = 3.07 x 109 dry lb/year • Assume 10% moisture by weight1 • Switchgrass composition to elemental balance. Switchgrass Feed Mass %5 lb/yr lbmol/yr C 48.8% 1.50E+09 1.25E+08 H 6.4% 1.97E+08 1.95E+08 O 36.3% 1.11E+09 6.95E+07 N 0.7% 2.21E+07 1.58E+06 S 0.0% 6.13E+05 1.91E+04 Ash 7.8% 2.39E+08 Moisture 11.0% 3.41E+08 1.89E+07 Total 1.1 3.41E+09 4.10E+08 GASIFIER MATERIAL BALANCE (cont.) • Assume a percent carbon conversion of 60%3 • Assume 40% moisture by vol. in the syngas6 • Balance carbon with syngas composition • Assuming 16g/m3 tars in the syngas1, model as ideal gas at 1500oF • Model tar as C10H8 for lbmol/yr calculation6 SynGas CO2 CO H2 CH4 C2H4 C2H6 H2O Tar Total Mol % lbmol/yr lb/yr 12.2% 1.09E+07 4.79E+08 44.4% 3.96E+07 1.11E+09 22.0% 1.96E+07 3.96E+07 15.6% 1.39E+07 2.23E+08 5.1% 4.55E+06 1.28E+08 0.7% 6.24E+05 1.88E+07 6.31E+07 1.14E+09 1.07E+06 1.38E+08 100.0% 1.53E+08 3.27E+09 GASIFIER MATERIAL BALANCE (cont.) Other Assumptions • No SOx or NOx formed in gasifier2 • 8.3% of S parsed to char; rest is 90% H2S and 10% COS6 • 6.6% of N parsed to char; rest is 25% NH3, 10% HCN, and 65% N2 6 • All chlorine becomes HCl2 Other Compounds lbmol/yr lb/yr H2S 1.58E+04 5.38E+05 COS 1.75E+03 2.11E+04 NH3 3.68E+05 6.27E+06 HCN 1.47E+05 3.98E+06 N2 4.79E+05 1.34E+07 HCl 3.36E+04 1.23E+06 Total 1.04E+06 2.54E+07 GASIFIER MATERIAL BALANCE (cont.) Final Balance to Char • A steam feed of 0.4 lb/lb dry biomass is assumed6 = 1.23 x 109 lb/yr = 6.81 x 107 lbmol/yr • Remaining hydrogen and oxygen outside of syngas are parsed to the char.6 • Ash from the switchgrass is inert and is parsed to the char.6 Ash SiO2 Al2O3 Fe2O3 MgO CaO Na2O K2O P2O5 Other lb/year 1.36E+08 1.91E+06 8.83E+05 1.14E+07 2.64E+07 7.16E+05 2.16E+07 1.31E+07 2.56E+07 COMBUSTOR MATERIAL BALANCE • The H, C, and S in the char are combusted with 20% excess air1 to heat the circulating SiO2. • The combustion products make up the flue gas while the inert ash is collected • All carbon forms CO2, H forms H2O, S forms SO2 and N forms N2 and NO2 in a 6:69 molar ratio7 Combustion Products lbmol/year CO2 N2 NO2 H2O SO2 Total 3.89E+07 4.79E+04 8.32E+03 5.82E+07 1.59E+03 9.72E+07 GASIFIER/COMBUSTOR ENERGY BALANCE • (heat of formation + sensible heat) products = (heat of formation + sensible heat) feeds • Heat of formation of switchgrass—subtract HHV of elements from HHV of fuel1 (7689 Btu/lb)5 s • Heat capacity of switchgrass is assumed to be 0.358 Btu/lboF8 • Other streams—Heats of formation are found along with Antoine Coefficients for calculation of heat capacities. • Beginning temperatures for calculation: ~500oF for the feed steam10,1 ~220oF for the switchgrass feed10 ~500oF for the air feed10 ~1900oF for the flue gas1 ~1500oF for the syn gas1 GASIFIER/COMBUSTOR ENERGY BALANCE Flue Gas lbmol/year ΔHf Total o 11 ΔHf o Btu/lbmol Btu/year Cp/R = A+BT+DT-2 A B 11 D Cp Sensible H Btu/lb F Btu/year N2 2.32E+08 0.00E+00 0.00E+00 3.28 0.593 0.04 2.66E-01 2.93E+12 O2 1.04E+07 0.00E+00 0.00E+00 3.639 0.506 -0.227 2.48E-01 1.40E+11 H2O 5.82E+07 -1.04E+05 -6.06E+12 3.47 1.45 CO2 3.89E+07 -1.69E+05 -6.59E+12 5.457 1.045 -1.157 2.75E-01 7.98E+11 NO2 7.86E+03 5.96E+04 4.68E+08 4.982 1.195 -0.792 2.50E-01 9.99E+07 SO2 1.59E+03 -5.34E+05 -8.48E+08 5.699 0.801 -1.015 1.91E-01 3.29E+07 • Total 0.121 enthalpy out in flue gas = 7.88 x 1012 Btu/year 5.11E-01 9.07E+11 COMPLETION OF ENERGY BALANCE • Assume 1% heat loss7 • Manipulate carbon conversion %, moisture of switchgrass, steam feed rate, air feed rate, and temperatures of all streams. • Balance until HIN = HOUT • Using ΔHrxn for the combustion of C, H, and S, and SiO2 heat capacity of 0.378 Btu/lb-oF: The sand is circulated at a rate of 1.13 x 1011 lb/yr or 37 lb/lb dry biomass SUMMARY OF GASIFIER STREAMS Syngas Out Switchgrass In T (oF) 1454 T (oF) 220 lb/yr 3.30E+09 lb/yr 3.41E+09 Btu/yr -9.13E+12 Btu/yr -1.13E+13 Flue Gas Steam In T (oF) 1770 T (oF) 700 lb/yr 9.60E+09 IN lb/yr 1.23E+09 -7.88E+12 1.31E+10 Btu/yr Btu/yr -6.73E+12 lb/yr Btu/yr -1.72E+13 Ash Air In T (oF) 1770 T (oF) 500 OUT lb/yr 2.37E+08 (-1% Heat Loss) lb/yr 8.50E+09 1.31E+10 Btu/yr -1.50E+10 Btu/yr 8.62E+11 lb/yr Btu/yr •All at 23 psia -1.72E+13 GAS CLEAN UP Examples of biomass tars C10 H 8 10 H 2 O 14 H 2 10CO C10 H 8 10CO 20CO 4 H 2 C10 H 8 10C 4 H 2 Chemical reactions for destruction of napthalene Component Mole flow CO2 1,360.29 CO 4,950.55 H2 2,452.98 CH4 1,739.38 C2H4 568.64 C2H6 78.05 Tars (C10H8) 135.55 H2O 7,889.32 TCCA-TAR CATALYTIC CRACKER A TCCB-TAR CATALYTIC CRACKER B Type: Fluidized bed with cyclone filters Type: Fixed bed with guard bed Catalyst: Calcined, nickel treated olivine Catalyst: Calcined dolomite Ash: 104.23 lb/hr Component Mole flow CO2 2,322.09 CO 6,373.06 H2 7,435.18 CH4 1,739.38 C2H4 0.00 C2H6 78.05 Tars (C10H8) 4.61 H2O 4,543.21 ALCOHOL SYNTHESIS - CATALYST SYNTHESIS OF ETHANOL FROM SYNGAS CATALYST: modified Fischer-Tropsch catalyst Molybdenum disulfied based promoted with alkali metal salts and cobalt Co/MoS2 High ethanol selectivity Catalytic activity: 13.5% conversion of CO (adding methanol recycle) ethanol yield: 25,900 lb/hr Product: mixture of linear alcohols Resistant to sulfur (up to 100ppm) H2S inlet stream to maintain catalyst activity Methanol decomposition functionality Methanol in feed is not detrimental to the reaction SYNTHESIS OF n-BUTANOL FROM BIOMOLECULAR CONDENSATION OF ETHANOL CATALYST: γ-alumina supported nickel 8%Ni/γ-Al2O3 γ-Al2O3 and solution of Ni(NO3)2·6H2O Dried at 150°C Pretreated under hydrogen flow at 500°C for 4 h n-butanol selectivity: 64.3% High catalytic activity: 19.1% conversion of ethanol n-butanol yield: 12.3% Low reaction temperature: 200°C Table: Catalytic performance over ethanol condensation reaction Catalyts AD Sel. (%) BD Sel. (%) 8%Ni/γAl2O3 5.8 3.8 EA BO Sel. (%) Sel. (%) 3.1 64.3 Others Sel. (%) 23.0 a) AD: Acetaldehyde; BD: Butaldehyde; EA: Ethanyl acetate; BO: nbutanol c) Others: 2-Ethylbutanol, n-hexanol, ethyl ether, n-butyl ether etc. ALCOHOL SYNTHESIS molybdenum-disulfide-based (MoS2) Langmuir-Hinshelwood kinetic approach Methanol Recycle Making Butanol is Difficult! Methanol recycle makes more Ethanol! Rh catalyst cost $5000/ounce Ethanol for Now • Make as much as possible • Look into options for Hydrogenation of Ethanol to make Butanol Ethanol Targets NREL Model Target 60% CO Conversion Alcohol Methanol Ethanol Propanol Butanol Pentanol Others Water Total NREL Model (wt%) 5.01 70.66 10.07 1.25 0.17 10.98 1.86 100 Langmuir-Hinshelwood kinetics System of Reactions for Mixed Alcohol Synthesis Rate Equations Water Gas Shift Reaction Parameters found Experimentally Parameter Methanol Ethanol Hydrocabo Propanol ns Units mol/hr/kg cat KJ/mol Am, Ae, Ap, Ah 14.6233 3.0518 0.2148 9.3856 Em, Ee, Ep, Eh 143.472 24.986 89.3328 95.416 nm, ne, np, nh 3 1 1 1 K1 7.64E-09 K2 0.6785 K3 0.9987 Ke 0.7367 Kp 0.6086 Kh 1.2472 Kz 0.8359 Tcp 598 Kelvin Pcpi 46.7*(xi) 46.7*(xi) 46.7*(xi) 46.7*(xi) atm Tcp and Pcpi are the temperature and partial pressure at the center point experiment. The center point experiment describes the basis for calculation of the above Parameters. Differential Equations input to Polymath With initial conditions Into Reactor Kmol/hr lb/hr Out of Reactor Kmol/hr lb/hr CO 2245.532 4950.551 766.3169 47321.2 CO2 6.170226 13.60302 38.7946 3764.064 H2 2601.05 5734.333 964.8306 4287.953 N2 27.13115 59.81394 H2O 3578.64 7889.552 27.13115 59.81394 1.258634 49.98825 CH3OH ~0 0 5.480634 387.1307 C2H5OH ~0 0 17.7324 1800.948 C3H7OH ~0 0 2.660657 352.5019 394.4755 869.6697 498.6421 17636.35 CH4 In H2/CO = 1.16 In CO2/CO = 0.0027 CO conversion ~65% Out H2/CO = 0.0906 Out CO2/CO = 0.080 Without Recycle 52100 barrels/yr BASIC COST ESTIMATION Rough Cost Scale-up Base Year Installed cost in 2005 ($) Installed cost in 2009 ($) 2002 $ 137,228,869 $ 222,999,612 Chemical Engineering Cost Index : Cost is scaled up from a ethanol production plant. REFERENCES 1. 2. 3. 4. 5. 6. 7. 8. Higman, C., van der Burgt, M., “Gasification.” 2003, Elsevier Science Silvagas Corporation, www.silvagas.com Paisley, M.A., Overend, R.P., “The Silvagas Process from Future Energy Resources—A Commercialization Success.” 2002. Bioenergy Feedstock Development Program. “Biofuels from Switchgrass: Greener Energy Pastures.” Oak Ridge National Laboratory. Laser, M., “Switchgrass Composition Methods.” Memo: 2004 Philips, S., Aden, A., Jechura, J., Dayton, D., “Thermochemical Ethanol via Indirect Gasification and Mixed Alcohol Synthesis of Lignocellulosic Biomass.” NREL: 2007 Basu, P., “Combustion and Gasification in Fluidized Beds.” Taylor and Francis Group: 2006 Kaliyan, Morey, “Strategies to Improve the Durability of Switchgrass Briquettes.” ASAE: 2007 REFERENCES (cont.) 10. Bain, R.L., “Material and Energy Balances for Methanol from Biomass Using Biomass Gasifiers.” NREL: 1992 11. Smith, J.M., Van Ness, H.C., Abbott, M.M., “Introduction to Chemical Engineering Thermodynamics.” 7th Ed. McGrawHill: 2005 12. Yang, K.W., Jiang, X. Z., Zhang, W. C. , “One-step Synthesis of n-Butanol from Ethanol Condensation over Alumina-supported Metal Catalysts.” Chinise Chemical Letters, 2004