amine grafted adsorbents for efficient co 2 capture
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Amine Grafted Adsorbents for Efficient CO 2 Capture. Dr Joe Wood School of Chemical Engineering University of Birmingham, UK. Midlands Energy Consortium International Showcase 5 th October 2011. Overview. Step-change Adsorbents For Carbon Capture - PowerPoint PPT PresentationTRANSCRIPT
Dr Joe WoodSchool of Chemical EngineeringUniversity of Birmingham, UK
Amine Grafted Adsorbents for Efficient CO2 Capture
Midlands Energy Consortium International Showcase 5th October 2011
Overview Step-change Adsorbents For Carbon Capture
Nottingham, Birmingham, UCL, Liverpool. Sponsors EPSRC & E.ON
Post-combustion capture Hydrotalcite clays Amine grafting TGA studies of CO2 uptake
Next Generation of Activated Carbon Adsorbents for the Pre-Combustion Capture of CO2 UK-China CCS Call
Nottingham, Birmingham, UCL, Warwick, Tsinghua Universities, Chinese Inst. Coal Chemistry. UK Sponsor EPSRC
Pre-combustion capture CO2 breakthrough curves gProms modelling
Post-Combustion TechnologyAbsorption in to liquid amines Hydrotalcite solid adsorbent
Moving bed adsorption schematic
Step Change Adsorbents for Carbon Dioxide Capture Aim: To develop advanced adsorbents capable of
capturing > 3 mmol/g CO2
Adsorbents should also have desirable kinetics, stability and ability to be regenerated
Performance Parameter TargetOperating Temperature (C)
: adsorption 40 – 60 C: desorption 85 – 140 C
Cyclic capacity >3 mmol g-1
Rate of adsorption Order of secondsOperating pressure 1015 mbarPressure drop of capture plant Ideally < 2 psiCO2 product purity >95 %CO2 capture (of total emissions) >80 %
Proposed operating conditions for capture plant based on a temperature swing adsorption process (Drage et al, J. Materials Chem 2011).
Hydrotalcite Clays
•Hydroxycarbonate of Mg and Al•Brucite (Mg(OH)2) layers•Mg2+ ions substituted by other metals•(CO3)2- ions in the interlayer
Improved exfoliation method
TolueneUS
90oC,24h
Adding certain amount of water (eg. 0.3ml/g)
Brucite like layer
Mg2+ or Al3+
OH
Si
NH2
Dodecyl sulfate
Harlick, P. and Sayari, A. Ind. Eng. Chem. Res. 2007, 46, 446-458.
Different Types of Aminosilanes
(3-Aminopropyl)triethoxysilane (N1)
N-(2-Aminoethyl-3-aminopropyl) trimethoxysilane (N2)
N-3-(Trimethoxysilyl)propyl) diethylenetriamine (N3)
Si
O
OO
NH2
Si
O
OO
NH
NH2
Si
O
OO
NH
NHNH2
CO2 Adsorption by TGA
0.0 20.0 40.0 60.0 80.0 100.0 120.0 140.086
88
90
92
94
96
98
100
0
20
40
60
80
100
120
MassTemp.
Time (min)
Mas
s (%
)
Tem
p (o
C)
Switch from N2 to CO2
CO2 adsorbed
Samples Prepared With Water –CO2 adsorption at 80 oC
0.00 0.05 0.10 0.15 0.20 0.25 0.30 0.35 0.40 0.450.00
0.50
1.00
1.50
2.00
2.50
3.00
3.50
N1N2N3
Water content (ml/g)
CO
2 up
take
(mm
ol/g
)
Next Generation of Activated Carbon Adsorbents for Pre-Combustion CO2 capture
Experimental Work
Experimental Work
Cycle 1 adjusted by 20% and cycle 2 by 10%
Zeolite X adsorbent
Equations Component Mass Balance
Adsorption rate equation
Approximated Langmuir equation
Assumptions Ideal gas law; Pressure drop by Darcy’s equation; Isothermal
operation; Bed in thermal equilibrium; No variation in radial direction
Modelling and Simulation
Modelling and Simulation
Decreasing Bed Length
Acknowledgements
EPSRC and E.ON Dr Jiawei Wang Dr Trevor Drage, Prof. Colin Snape and
STEPCAP project partners Simon Caldwell, Dr Bushra Al-Duri