CO 2 Capture by Amine Scrubbing

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CO 2 Capture by Amine Scrubbing By Gary T. Rochelle Luminant Carbon Management Program Department of Chemical Engineering The University of Texas at Austin US UK workshop May 9, 2010

Roadmap Research on Amine Scrubbing Objectives and Scope Goals Conclusions on Energy Amine Scrubbing is THE Process Conclusions on Solvent Management Amine Scrubbing is THE Process R&D needs for amine scrubbing

Objectives of the Luminant Program Train graduate & undergraduate students Create understanding, data, & methods to facilitate deployment of CO 2 capture Create innovations to enhance performance and reduce cost of CO 2 capture

Strategy Apply ChE science to understand & quantify the performance of MEA absorption/stripping Energy Performance Solvent Management Develop evolutionary innovations Better Processes Better Solvents

Annual Funding by Important Sponsors Current $500k Luminant Energy $800k 29 companies $800k State of Texas ovhd & faculty $2100k Total Annual Program Funding Pending $350k NRG/DOE, pilot & tech support $325k CO 2 capture pilot plant project (C2P3) $1000k DOE (w URS & Trimeric), pilot testing

Energy Science Thermo and Rates FTIR: P CO2, P amine : 30-70C, 120-160C P t : 120-160C Wetted Wall Column: P CO2, k g : 40-100C C p by DSC, Speciation by NMR Packing Characterization in 18-inch column a (CO 2 ), K g a (SO 2 ), k l a (toluene) AspenPlus Process Modeling Thermo by Electrolyte NRTL Diffusion & kinetics by RateSep Dynamics by ACM Validation by 18-inch absorber/stripper Air/CO 2

Science of Solvent Management Oxidative Degradation With FTIR 1-5 days 40-70C 1-4 weeks, low gas flow, 40-70C Cyclic: 2 weeks, 70-130C Thermal degradation - cylinders at 100-175C Nitrosoamine production & analysis Amine Volatility by FTIR Reclaiming: Thermal, Sulfate Crystallization Analytical tools HPLC: cation, anion, aminoacid, molecule MS with HPLC, cation, GC

Process Innovation Goals Use Heat rather than mechanical compression Strip at 120-150 o C, limited by degradation Reversible Stripping high lean ldg, 0.3-0.4 Maximize Heat Reversibility at stripper Cross Exchanger & Reboiler DT=5 o C 2-stage flash, matrix, multip, or interheat Vapor recompression Minimize T of Absorption, 30-40 o C Precooling & intercooling Gas & Solvent Control water balance Simplify

Solvent Innovation Goals Cost <$5/lb, one step past MEA CO 2 Rate >MEA Heat of Absorption >70 kj/mole T Stability >140 o C Reversible Capacity >0.8 mole/kg Viscosity <15 cp No solid or liquid phase separation Low oxidative degradation Volatility=10-30 ppm, allows reclaiming

Intense Work Solvents 7 to 11 m (30-40%) MEA 8 m (40%) Piperazine (PZ) 7 m MDEA/2 m PZ (50 wt) Piperazine Derivatives Screening Aminoacids Hindered amines DGA, EDA, MAPA

Conclusions on Energy

Irreversibilities CO 2 22 Absorb 40 o C 14 8 m PZ 25 150 o C 17 bar 34 150 o C 11 bar 11 W ideal = 113 kwh/tonne, W real =219 kwh/tonne

W (kwh/tonne CO2) Equivalent Work of Amine Scrubbing 500 400 300 200 100 W equiv 0.75Q T stm T T stm sink W comp MEA PZ Minimum Work = 113 kwh/tonne Separation & Compression to 150 bar W pump 0 2000 2004 Year 2008

Separation Efficiency, W min /W (%) CO 2 capture by 8 m PZ (2-stage regeneration at 150 o C) Cryogenic air separation (Darde et al., 2008) Hydrocarbon Distillation (relative volatility=1.1 to 5) Desalination by reverse osmosis (Semiat, 2008) 50 25 10-36 21

Capture processes driven by mechanical compression are not competitive Minimum Work (Isothermal, ideal compression) Work (kwh/tonne) Efficiency (%) 111 100 PZ with 2-stage regeneration at 150C 219 50 Ideal process driven by real compression 72% eff, 40 o C cooling, P j /P j-1 =2 (Ideal Membranes or PSA) 206+ 55 Oxycombustion with Ideal air separation 217+ 52 Real compressors for Air & CO 2 1.35 moles O 2 /mole CO 2 Real Oxycombustion (Darde et al., 2008) 284 40

Thermal Swing Regeneration of solids requires difficult equipment. Low absorption T with high heat of absorption Solids regeneration at high pressure Cross exchange at DT=5 o C And low cost, robust solids

Conclusions Research on Solvent Management MEA is inexpensive & stable to 120C but degrades readily with O 2 or high T PZ is more expensive but stable to 150C & oxidizes slowly Both are reclaimed by evaporation

High cost reagents or materials may not survive coal flue gas Continuous & intermittent impurities SO 3, SO 2, HCl, fly ash, NO x, O 2, H 2 O Fe +2, Cr +3, gypsum, CaCO 3, T excursions High cost materials must be reclaimable High cost materials will require costly pretreating Most likely a fatal flaw for anything >$5/lb Designer amines Enzymes Ionic liquids Membranes Most organic & inorganic adsorbents/absorbents Nanomaterials

Some R&D Needs for Amine Scrubbing Solvent Management Nitrosamines, aldehydes, land other toxics Oxidative Degradation Reclaiming Pilot plant testing with coal flue gas Energy Inexpensive solvents with greater heat of absorption Inexpensive solvents stable to higher T Scale-up Advanced strippers Absorbers Exchangers: Reboilers, Exchangers Steam Extraction Pretreating & water balance

History Repeats CaCO 3 Slurry:::Amine Scrubbing CaCO 3 Event Amine 1948 1 st commercial plant 1980 1970 Too commercial for Gov. support But too costly, too dirty to use 1990 1970-82 Government funds advanced alts 1995-1975-85 Govern. & EPRI fund test facilities 2010-1977 Power Industry deploys 500+ MW 2016? 2009 First choice dominates 2030?

A Newer System to Reduce cost by 10-20% 8 m (40 wt%) Piperazine 10-20% less energy than 30 wt% MEA 2 x CO 2 mass transfer rate 1.8 x capacity High P (6 15 atm) Stripper, stable to 150 C Oxidatively stable, esp. with Inhibitor A Less volatile than 7 m MEA Good Opportunities for Reclaiming

Economic Perspective Capture is $50-75/tonne CO2 ($50-75/MWH) Wholesale power doubles ($50 to 100/MWH) Breakeven w Gas at $70/MWH (capture $50) Existing plants, fuel + capture Coal @$2/MMBtu Gas @ $4.50/MMBtu Gasoline @ $0.40/gal = $50/Tonne CO 2

Aqueous Abs/Str: Near commercial 100 s of plants for treating H 2 & natural gas MEA and other amine solvents 10 s of plants with natural gas combustion Fluor, 30% MEA MHI, KS-1 A few plants with coal combustion Abb-Lummus, 20% MEA, 6, 8, & 33 MW Fluor, 30% MEA, (6 MW) MHI, KS-1 (7 & 25 MW) Still need coal on 800 MW

One Conclusion on Energy 8 m PZ (40 wt%) with 2-stage Flash at 150oC 10-20% less energy than 30 wt% MEA 2 x CO 2 mass transfer rate 1.8 x capacity Stable to 150 o c Stripping at 11 & 17 atm W min /W actual = 50% efficiency

Tail End Technology Ideal for Development, Advantages Demonstration, of post combustion & Deployment Low risk Independent, separable, add-on systems Failures impact only Capture and Sequestration Permits on/off operation to address peak load Low cost & less calendar time Develop and demonstrate with add-on systems Less demo cost than integrated systems Resolve problems in small pilots with real gas Demo Full-scale absorbers w 100-200 MW gas Ultimately 800 MW absorbers

Amine Scrubbing (Bottoms, 1930) 30 wt% MEA CO 2 Packed Absorber 1 bar DT=5C Stripper 2 bar Packing or Trays 12% CO 2 5% O 2 0 ppm SO 2 40 o C 115C Reboiler 45 psig stm