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Post Combustion Capture Conference 2011, Abu Dhabi 17-19 May 2011 Solvent comparison for postcombustion CO 2 capture Peter Brder, Hallvard F. Svendsen Norwegian University of Science and Technology Basic characterization of the amine CO 2


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SLIDE 1

Solvent comparison for postcombustion CO2 capture

Peter Brúder, Hallvard F. Svendsen Norwegian University of Science and Technology Post Combustion Capture Conference 2011, Abu Dhabi 17-19 May 2011

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SLIDE 2

Basic characterization of the amine – CO2 systems

  • Density (loaded / unloaded)
  • Viscosity (loaded / unloaded)
  • Amine volatility
  • Physical solubility of CO2 in the water-amine solution
  • Reaction rate amine – CO2
  • Maximum rich and minimum lean loading (cyclic capacity)
  • Stripping specific heat consumption
  • Partial CO2 pressure over the loaded solution
  • Environmental impact of the amine
  • Thermal and oxidative degradation of the amine
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SLIDE 3

Screening equipment

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SLIDE 4

Screening procedure

  • The absorption temp. is 40 0C, the stripping occurs at 80 0C
  • The system is flushed with N2 before the measurements
  • The calibration is done for 0 % and 10 % CO2
  • The outlet gas from the sample is analysed by IR detector
  • After the end of absorption and desorption the density of the

samples were measured, and samples were taken for titration of CO2

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SLIDE 5

Tested chemicals

Solvent CAS pKa Structure Comment 2-Amino-2- (hydroxymethyl)- 1,3-propanediol (TRIS) 77-86-1 8.1 DMMEA 108-01-0 9.2 AMP 124-68-5 9.7 DEEA 100-37-8 9.8 Piperazine 110-85-0 9.8 Ethanolamine (MEA) 141-43-5 9.5 3-amino-1- methylaminopropan e (MAPA) 6291-84-5 10.5

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SLIDE 6

Tested concentrations (A:B)

A B Piperazine MEA MAPA 5 5 TRIS 3:1 3:1 3:1 DMMEA 3:1, 5:2 5:2 3:2, 5:2, 5:1 AMP 3:1 3:1 DEEA 3:1 5:2 5:2, 4:4

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SLIDE 7

Results

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SLIDE 8

Absorption rates

0,1 0,2 0,3 0,4 0,5 0,6 1 2 3 4 5 load [mol CO2/kg solution] Absorbtion rate [Nl/min] 3M AMP + 1M PZ 08.08 2008 3 M AMP + 1 M MAPA 06.10 2008 3 M DMMEA + 1 M PZ 20.08.2008 3 M DMMEA + 2 M MAPA 09.10 2008 5 M DMMEA + 2 M PZ 21.08 2008 5 M DMMEA + 2 M MEA 3.09 2008 5 M DMMEA + 2 M MAPA 4.09 2008 5 M DMMEA + 1 M MAPA 23.03 2010 3 M DEEA + 1 M PZ 15.09 2008 5 M DEEA + 2 M MEA 01.10 2008 3 M TRIZMA + 1 M PZ 17.09 2008 3 M TRIZMA + 1 M MEA 22.09 2008 3 M TRIZMA + 1 M MAPA 23.09 2008 30 % MEA 02.10 2008 5 M MAPA 13.10 2008

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SLIDE 9

Lean loading - to final 1 kPa CO2, 80 0C (titration)

Concentration [mol/l] System Lean loading [mol CO2/kg sol] 5 MAPA 1.08 3 : 2 DMMEA : MAPA 1.68 5 : 2 DMMEA : PZ 2.41 5 : 2 DMMEA : MAPA 1.93 3 : 1 AMP : PZ

  • 3 : 1

AMP : MAPA 1.65 3 : 1 DEEA : PZ

  • 5

MEA 0.95 5 : 2 DMMEA : MEA 1.79 3 : 1 DMMEA : PZ 1.82 3 : 1 TRIS : MAPA 0.79 3 : 1 TRIS : PZ 1.06 5 : 2 DEEA : MEA

  • 3 : 1

TRIS : MEA 0.77

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SLIDE 10

Cyclic loading calculation

  • The cyclic loading from screening values are always bigger than

the values from the titration (average ~ 11 %)

  • Experimentally for MEA ~ 90 % of the equilibrium loading can be

reached during absorption, corresponding an absorber bottom mass transfer rate of about 0.2 Nl/min

  • Two values for cyclic loading were calculated, one based on the

end point of the absorption curves, and the other based on an end pointdetermined by a minimum mass transfer rate

  • f 0.2 Nl/min
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SLIDE 11

System comparison

1 2 3 4 5 6 7 8

5MAPA 3DMMEA/2MAPA 5DMMEA/2PZ 5DMMEA/2MAPA 3AMP/1PZ 3AMP/1MAPA 3DEEA/1PZ 5MEA 5DMMEA/2MEA 3DMMEA/1PZ 3TRIS/1MAPA 3TRIS/1PZ 5DEEA/2MEA 3TRIS/1MEA

total amine mol/l Absorbed CO2 titration mol/kg sol Cyclic capacity total mol/kg sol Cyclic capacity 80 C (Loading 0,2 Nl/min - Lean loading) mol/kg sol

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SLIDE 12

Absorbent evaluation

  • MAPA has the lowest cyclic capacity between the tested

promotors compared to the total loading

  • 5 DMMEA : 2 MEA has approximately the same cyclic and total

capacity as 3 DMMEA : 1 PZ, but with a much slower kinetics

  • AMP with PZ has much better kinetics than MAPA
  • Tris and DMMEA perform worst with MEA from the three

promotors

  • Despite of the lower amine concentration, the 3 DMMEA : 2

MAPA has higher kinetics and total absorption in the final stage than the 5 DMMEA : 2 MAPA/PZ systems, probably due to the lower viscosity, however the cyclic concentration is lower

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SLIDE 13

Absorption rates for phase change systems

0,1 0,2 0,3 0,4 0,5 0,6 1 2 3 4 5 6 load [mol CO2/kg solution] Absorbtion rate [Nl/min] 5 M DEEA + 2 M MAPA 16.09 2008 30 % MEA 02.10 2008 4 M DEEA + 4 M MAPA 08.10 2008 5 M MAPA 13.10 2008

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SLIDE 14

DEEA:MAPA 5:2

Unloaded solution Loaded solution with separated phases Upper phase Lower phase

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SLIDE 15

DEEA:MAPA 5:2

~ 60 vol % ~ 0,91 kg/l ~ 0,25 mol CO2/kg ~ 8,1 mol NH2/kg ~ 40 vol % ~ ??? kg/l ~ 4,8 mol CO2/kg ~ 9,9 mol NH2/kg The prepared unloaded solution in %: DEEA : MAPA : H2O Mol %: 33 : 13 : 54 Mass %: 64 : 20 : 16 Vol %*: 65 : 20 : 15

* Density for the calculation has been taken from chemical description

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SLIDE 16

DEEA:MAPA 5:2

At 40 0C

  • The 2 phases (layers) are separated immediately after the end of the

experiment, but to reach better separation, needs 1 – 2 days at 20 0C

  • Seems that two phases are formed for DEEA : MEA too, but after

mixing only 1 phase remains, and this is stable

  • The system 4:4 was also tested, but the lower phase is very viscous

and in other cases the viscosity doesn’t allow formation of 2 layers

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SLIDE 17

Conclusion

  • Mixed solvents seems to have better performance than

the single ones

  • The kinetics of the reaction can be effected significantly

with the increasing viscosity during the CO2 absorption

  • These two results imply significantly reduced stripping

steam consumption, sensible heat loss, and around half of the solvent circulation rate in a plant operation compared to MEA.

  • The liquid phase separated systems seems to have a

better kinetics, probably due to the increased contact area

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SLIDE 18

Acknowledgements

The research leading to these results has received funding from the European Community’s Seventh Framework Program FP7/2007-2011 under grant agreement nº 213569 (CESAR).

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SLIDE 19

Thank you !