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Post-combustion CO2 capture from natural gas combined cycles by solvent supported membranes 
Alberto Volenoa, Matteo C. Romanoa, Davide M. Turia, Paolo Chiesaa, 
Minh T. Hob, Dianne E. Wileyb 
a Politecnico di Milano, Department of Energy, Milan, Italy 
b CO2CRC, University of New South Wales, Sydney, Australia 
GHGT-12, Austin, TX, USA – 6-9th October 2014
2 
Integration in NG combined cycles 
NGCC flue gas: 
• 
CO2 concentration ~ 4% 
• 
N2/CO2 ~ 19  large surface and low CO2 purity with a simple post- combustion capture configuration 
NGCC with flue gas recycle: 
• 
CO2 concentration ~ 8-10% 
• 
N2/CO2 ~ 10  smaller surface, but still low CO2 purity (purification step required)
3 
Integration in NG combined cycles 
Alternative configuration with selective CO2 flue gas recycle 
Merkel TC, Lin H, Wei X, Baker R. J Membr Sci 2010;359:126-139. 
e.me.mCO2CO2Flue gas ventedair / flue gasfuelCO2water/steam~ Gas turbineSteam turbineHRSG~ HPevaIPevaLPecoIPrhHP sh IPecoHPecoIPshHPecoLPevaLPshmemb. 2memb. 1CO2to storageNatural gasFlue gas coolere.m 
At memb.1 inlet: 
• 
CO2 concentration ~ 33-35% 
• 
N2/CO2 ~ 1.7
4 
Results 
Sensitivity analysis on membrane feed pressure: 
Ref. NGCC Membrane cases Membrane feed pressure, bar 1.52 2.03 3.04 4.05 Power balance, MW: Gas turbine net power 272.1 249.8 249.4 249.2 249.0 Steam turbine gross power 147.1 167.3 167.6 167.7 168.0 Steam cycle pumps -1.79 -2.13 -2.14 -2.14 -2.15 Aux. for cond. heat rejection -1.86 -2.05 -2.05 -2.05 -2.05 Aux. for heat reject. other than cond. -0.77 -0.82 -0.90 -0.98 Fresh air fan -2.08 -2.05 -2.03 -2.01 Flue gas compressor -25.55 -45.44 -76.60 -100.8 Flue gas expander 11.65 21.25 36.46 48.03 CO2 compression -19.20 -19.02 -18.89 -18.59 Gross Power, MW 419.2 417.1 417.0 417.0 416.9 Net Power, MW 415.6 376.9 366.7 350.8 338.4 Heat input, MW, LHV 711.3 711.3 711.3 711.3 711.3 Net efficiency, %LHV 58.4 53.0 51.6 49.3 47.6 CO2 capture efficiency, % 90.0 90.0 90.0 90.0 Specific emission, kg/MWh 353.7 40.3 41.5 43.3 44.9 CO2 avoided, % 88.6 88.3 87.8 87.3 SPECCA, MJ/kg 2.01 2.63 3.66 4.55 CO2 purity, %mol dry 95.2 96.0 96.5 96.7
5 
Economic analysis - Results 
Cost of CO2 avoided 
020406080100120p_f=1.5barp_f=2barp_f=3barp_f=4barCost of CO2avoided, US$/t Other OpexEnergy OpexCapex - otherCapex - CO2 compr. andtreatm. Capex - flue gas compr./exp. Capex - membranes 
73.5 $/t 
DOE-NETL MEA baseline: 96 $/t DOE/NETL, 2012. Updated Costs (June 2011 Basis) for Selected Bituminous Baseline Cases.
6 
Conclusions 
 
Economic analysis is needed to define the optimal operating parameters of CO2 membrane systems 
 
Optimal operating parameters will depend on the membrane properties (permeability, selectivity) and cost 
 
Techno-economic analysis is a fundamental tool to correctly tailoring the properties of solvent supported membranes to specific applications 
 
Low efficiency penalties (-5.4% pts.) and competitive cost of CO2 avoided (73 $/t) have been obtained for this specific application, with membrane performance and cost in line with state-of-the-art polymeric membranes. 
 
It is likely that existing GT turbines cannot operate with CO2-enrichment as high as obtained with this configuration  The development of tailored GTs is challenging in absence of a sufficient market  limited retrofitability in existing NGCC. 
 
Easier integration and retrofitability in PC plants and other industrial sources (e.g. cement and iron & steel plants) is foreseen for CO2 membranes.
7 
MCFC as post-combustion CO2 separation systems
8 
MCFC technology can be utilized in cement plant for CO2 separation from fue gases at the preheating tower outlet, and for power production. 
 
Anode side fed with natural gas (direct and indirect internal reforming); 
 
Cathode side fed with fuel gases (@33-34% CO2) and additional air, providing O2. 
MCFC in cement plant 
CO2 from cement plant 
CO2 from NG 
CO2 to storage 
CO2 to asmosphere 
CH4+4CO32-2H2O+5CO2+2e- 
2O2+4CO2+8e- 4CO32- 
CO32-
9 
Q LHV, in [MWLHV] 
178.4 
MCFC LHV efficiency 
52.8 
Air utilization factor [UO2,%] 
39.3 
CO2 Utilization factor [UCO2,%] 
70 
Fuel cell power [MWE] 
106.1 
ORC Power [MWE] 
8.31 
Auxiliares [MWE] 
-19.86 
Overall net power [MWE] 
94.58 
Net electric LHV efficiency 
53.0 
Cement plant flue gas CO2 capture efficiency [%] 
73.2 
Equivalent CO2 emissions from NG conversion [g/kWh] 
-1061 
MCFC in cement plant - performance 
• 
Clinker production = 3600 tpd 
• 
MCFC voltage = 0.8 V

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Post-combustion CO2 capture from natural gas combined cycles by solvent supported membranes

  • 1. Post-combustion CO2 capture from natural gas combined cycles by solvent supported membranes Alberto Volenoa, Matteo C. Romanoa, Davide M. Turia, Paolo Chiesaa, Minh T. Hob, Dianne E. Wileyb a Politecnico di Milano, Department of Energy, Milan, Italy b CO2CRC, University of New South Wales, Sydney, Australia GHGT-12, Austin, TX, USA – 6-9th October 2014
  • 2. 2 Integration in NG combined cycles NGCC flue gas: • CO2 concentration ~ 4% • N2/CO2 ~ 19  large surface and low CO2 purity with a simple post- combustion capture configuration NGCC with flue gas recycle: • CO2 concentration ~ 8-10% • N2/CO2 ~ 10  smaller surface, but still low CO2 purity (purification step required)
  • 3. 3 Integration in NG combined cycles Alternative configuration with selective CO2 flue gas recycle Merkel TC, Lin H, Wei X, Baker R. J Membr Sci 2010;359:126-139. e.me.mCO2CO2Flue gas ventedair / flue gasfuelCO2water/steam~ Gas turbineSteam turbineHRSG~ HPevaIPevaLPecoIPrhHP sh IPecoHPecoIPshHPecoLPevaLPshmemb. 2memb. 1CO2to storageNatural gasFlue gas coolere.m At memb.1 inlet: • CO2 concentration ~ 33-35% • N2/CO2 ~ 1.7
  • 4. 4 Results Sensitivity analysis on membrane feed pressure: Ref. NGCC Membrane cases Membrane feed pressure, bar 1.52 2.03 3.04 4.05 Power balance, MW: Gas turbine net power 272.1 249.8 249.4 249.2 249.0 Steam turbine gross power 147.1 167.3 167.6 167.7 168.0 Steam cycle pumps -1.79 -2.13 -2.14 -2.14 -2.15 Aux. for cond. heat rejection -1.86 -2.05 -2.05 -2.05 -2.05 Aux. for heat reject. other than cond. -0.77 -0.82 -0.90 -0.98 Fresh air fan -2.08 -2.05 -2.03 -2.01 Flue gas compressor -25.55 -45.44 -76.60 -100.8 Flue gas expander 11.65 21.25 36.46 48.03 CO2 compression -19.20 -19.02 -18.89 -18.59 Gross Power, MW 419.2 417.1 417.0 417.0 416.9 Net Power, MW 415.6 376.9 366.7 350.8 338.4 Heat input, MW, LHV 711.3 711.3 711.3 711.3 711.3 Net efficiency, %LHV 58.4 53.0 51.6 49.3 47.6 CO2 capture efficiency, % 90.0 90.0 90.0 90.0 Specific emission, kg/MWh 353.7 40.3 41.5 43.3 44.9 CO2 avoided, % 88.6 88.3 87.8 87.3 SPECCA, MJ/kg 2.01 2.63 3.66 4.55 CO2 purity, %mol dry 95.2 96.0 96.5 96.7
  • 5. 5 Economic analysis - Results Cost of CO2 avoided 020406080100120p_f=1.5barp_f=2barp_f=3barp_f=4barCost of CO2avoided, US$/t Other OpexEnergy OpexCapex - otherCapex - CO2 compr. andtreatm. Capex - flue gas compr./exp. Capex - membranes 73.5 $/t DOE-NETL MEA baseline: 96 $/t DOE/NETL, 2012. Updated Costs (June 2011 Basis) for Selected Bituminous Baseline Cases.
  • 6. 6 Conclusions  Economic analysis is needed to define the optimal operating parameters of CO2 membrane systems  Optimal operating parameters will depend on the membrane properties (permeability, selectivity) and cost  Techno-economic analysis is a fundamental tool to correctly tailoring the properties of solvent supported membranes to specific applications  Low efficiency penalties (-5.4% pts.) and competitive cost of CO2 avoided (73 $/t) have been obtained for this specific application, with membrane performance and cost in line with state-of-the-art polymeric membranes.  It is likely that existing GT turbines cannot operate with CO2-enrichment as high as obtained with this configuration  The development of tailored GTs is challenging in absence of a sufficient market  limited retrofitability in existing NGCC.  Easier integration and retrofitability in PC plants and other industrial sources (e.g. cement and iron & steel plants) is foreseen for CO2 membranes.
  • 7. 7 MCFC as post-combustion CO2 separation systems
  • 8. 8 MCFC technology can be utilized in cement plant for CO2 separation from fue gases at the preheating tower outlet, and for power production.  Anode side fed with natural gas (direct and indirect internal reforming);  Cathode side fed with fuel gases (@33-34% CO2) and additional air, providing O2. MCFC in cement plant CO2 from cement plant CO2 from NG CO2 to storage CO2 to asmosphere CH4+4CO32-2H2O+5CO2+2e- 2O2+4CO2+8e- 4CO32- CO32-
  • 9. 9 Q LHV, in [MWLHV] 178.4 MCFC LHV efficiency 52.8 Air utilization factor [UO2,%] 39.3 CO2 Utilization factor [UCO2,%] 70 Fuel cell power [MWE] 106.1 ORC Power [MWE] 8.31 Auxiliares [MWE] -19.86 Overall net power [MWE] 94.58 Net electric LHV efficiency 53.0 Cement plant flue gas CO2 capture efficiency [%] 73.2 Equivalent CO2 emissions from NG conversion [g/kWh] -1061 MCFC in cement plant - performance • Clinker production = 3600 tpd • MCFC voltage = 0.8 V