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WTERT R h U d tWTERT Research UpdateGasification of Biomass
Solid Carbon Conversion
Marco J. CastaldiDepartment of Earth & Environmental EngineeringHenry Krumb School of Mines, Columbia University
WTERT 2008 Bi-Annual MeetingColumbia UniversityNew York, NY 10027
WTERT 08, New York, NY
October 16th and 17th
The Future
• Fossil Fuels will play smaller role
• Renewable / indigenous fuels will
become more prominentbeco e o e p o e t
• Carbon management is here to stay
WTERT 08, New York, NY
The NeedThe Need
• Carbon Neutral Energy ProductionCarbon Neutral Energy Production• Clean chemical (H2) Production
Z i i th CO t ti• Zero emissions more than CO2 sequestration• Reduce the dependence on single feedstock
• Indigenous source of fuel, distributed sources
• Power and chemicals produced from waste/biomass must be economically attractive as compared to current sources.
WTERT 08, New York, NY
Investment (wall Street)• Socially responsible investing• Emissions control (CO2)Emissions control (CO2)• Eco-friendly business practices
W ld E i F• World Economic Forum– Businesses need to reduce the negative impact on
h ithe environment“Many companies are now discovering that there my a be a strong correlation between ‘doing good’ and ‘doing well’”between doing good and doing well
“The next turn of the market wheel may reward companies with strong free cash flow as well as innovative companies thinking green”
WTERT 08, New York, NY
Alger Market Commentary March 31, 2007
Bioenergy
Source: IEA
WTERT 08, New York, NY
Municipal Solid Waste (MSW)• ~ 220 million tons of waste generated per year (U.S.)• Landfills are filling up• Disposal costs and energy costs are going up• Greenhouse gas initiatives (RGGI, etc)
•Waste as fuel emits 2/3 less CO2 than fossil fuel
Potential to replace ~ 20% of oil imports per year
Burning is good (WTE); instead of oil use waste
oil imports per year
Burning is good (WTE); instead of oil use waste• Gasification gives options
•choice of products – Heat, fuels, chemicals
WTERT 08, New York, NY
Chemicals From WasteChemicals From Waste• Military MISER program
– Trash/Biomass/Solid hydrocarbons to fuels– Trash/Biomass/Solid hydrocarbons to fuels
• American Chemical Society (ACS)– Letters to the editor – “chemicals from waste”
• C&EN April 2006
• Discover Magazine –– “DATA” Section : The Ultimate Garbage Disposal
• How to turn trash into clean energy – Geoplasma UnitHow to turn trash into clean energy Geoplasma Unit– 160 MW by 2009, St. Lucie County, Florida
• EnerChem/City of Edmonton 2008
WTERT 08, New York, NY
• EnerChem/City of Edmonton - 2008
CO2 & Waste / BiomassEnhanced gasification
WTERT 08, New York, NY
Catalytically Controlled Reaction y yGasifier (CRG Process)
O2
COsplit
O2
CoalH O2
CO2(optional)
H2
H2
CO H2
COout
H2
COH O2
AshH2
AshSeparator
H OSep.
2
CO+O to CO2 2
CO2
SOFCCO2
Carbon2
COH OAsh
2
H O2CO
Ashto waste stream H O2 CO2
recycle2
WTERT 08, New York, NY
H O Make up (optional)2
Castaldi MJ, Dooher JP. Int J Hydrogen Energy (2007), 37, 4170 - 4179
CRG Aspen™ SimulationCRG Aspen Simulation
CO PROD
CO-SPLIT
CO-ELECCMBSTOR
O2-COMB
COMBOUT
CO2RECYL
CO2EXHST
CO-PRODCO-COMB
CO2RETRN
C-IN
REF-PROD
H2-SEP
COOLDOWN COOLPROD H2O-PROD
REFORMERWATER-IN
H2-PROD
WTERT 08, New York, NY
Castaldi MJ, Dooher JP. Int J Hydrogen Energy (2007), 37, 4170 - 4179
1.2H2 Production, basis:0.5 kmol/hr C
ate
(kg/
hr)
0.8
1.0s/c:1.0, r:0
Baseline simulation results of energy balance and hydrogen
H2 F
low
ra
0 2
0.4
0.6generation for CRG process
Conventional Gasifier
0.0
0.2
10
20
Energy Requirements
H2O/C = s/c, CO2 recyc = rConventional Gasifier
H2 0.7 kg/hrCO2 ~ 15%
CRG P
y (M
J/hr
)
0
10Energy req'd by gasifierbalanced by CO combustion
CRG ProcessH2 0.85 kg/hrCO2 ~ 1.5%
e- ~13 kW/kmol C
Ene
rgy
-20
-10s/c:1.0, r:0CO Combustion ~48%
WTERT 08, New York, NY CO Split (to combustor)
0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9-30
Castaldi MJ, Int J Hydrogen Energy (2007), 37, 4170 - 4179
1.0
1.2H2 Production, basis:0.5 kmol/hr C
s/c:1.0, r:0.25
Flow
rate
(kg/
hr)
0.6
0.8s/c:1.0, r:0
H2 F
0.2
0.4
H2O/C = s/c, CO2 recyc = r
Comparison of baseline and 25% CO2 recycle to the
reformer0.0
10
20
Energy Requirements
Energy req'd by gasifierCRG Process
H 0 95 kg/hr
nerg
y (M
J/hr
)
-10
0
s/c:1.0, r:0
balanced by CO combustionH2 0.95 kg/hrCO2 ~ 1.5%
e- ~13 kW/kmol CCO Combustion ~42%
E
-20
s/c:1.0, r:0.25
WTERT 08, New York, NY
CO Split (to combustor)
0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9-30
Castaldi MJ, Int J Hydrogen Energy (2007), 37, 4170 - 4179
Experimental Feedstock Tested
BiomassCoalWaste
WTERT 08, New York, NY
Experimental Mass Decomposition Curve
1.00•250-400oC: Primary Reaction
• Bulk mass loss• Devolatilization and pyrolysis
0.60
0.80
actio
n
GrassesGrasses
•400-700oC: Secondary Reaction• Ligno-cellulosic gasification
Coals
0.40
Mas
s Fra
•700-900oC: Tertiary Reaction • Oxygen in feedstock & steam react with
lid b
0 00
0.20
WoodsWoods
solid Carbon• Recycled CO2 begins char burnoutMSW
0.000 200 400 600 800 1000
Temperature oC •950 - 1000oC Mass burnout complete• Higher residual correspond to lower
WTERT 08, New York, NY
g plignin content
Butterman and Castaldi, Env. Eng. Sci (2007) 22, 31-44
CO2 Impact on Coal
• Decrease in H2d ti ith COproduction with CO2
• Increase in CO production with CO2
WTERT 08, New York, NY
MSW DATAMSW DATAMass % vs Temp for Varius Amounts of CO2100
80 20
25Area 1: water volatilization
20
25
Area 2: biomass degradation
ass %
60
5
10
15
5
10
15
Ma
40
20% CO210% CO2
700 750 800 850 900 950 10000
Area 3:
700 750 800 850 900 950 10000
0
20 5% CO22.5% CO2Inert1% CO2
Area 3: petrochemical degradation
Area 4: boudouard reaction (C O2 + C 2C O)
WTERT 08, New York, NY
Temperature (oC)0 200 400 600 800 1000
0
CO i t ifi ti d tCO2 impact on gasification products1.00
CO2 Variation0.020
CO2 Variation
0-1)
0 40
0.60
0.80 0% 5%10%15%20%30%
40%
2
1 )
0.015
0% 5%10%15%20%40%50%
CO2 Variation
Mol
e Fr
actio
n (1
0
0.04
0.20
0.40 40%50%
ole
Frac
tion
(10-1
0.010
Increasing CO2
Increasing CO2
CO
M
0 01
0.02
0.03
H2 M
o0.005
Increasing CO2
Reactor Temperature (oC)
200 400 800 900 10000.00
0.01
R T (oC)
600 700 800 900 10000.000
WTERT 08, New York, NY
Reactor Temperature ( C)Fi 1 H d i i h CO ifi i
Reactor Temperature (oC)
CO increases with CO2 H2 decreases with CO2
H2/CO (Syngas) Tuning• Fuels • Chemicals• Combustion
3.0 SOFC operation• Combustion• Fuel cells
2.5
p
Gas Turbine Combustion – Low NOx operation/good stability
1.5
2.0
H2/C
O
Fisher Tropsch – petroleum/diesel fuels
Fisher Tropsch – Fe-based Catalyst – low molecular weight
1.0
H Co-based – more aromatic
specialty chemicals - dimethyl ether
0.0
0.5
WTERT 08, New York, NY
0 10 20 30 40 50
%CO2
Structural Components of BiomassCellulose- the main structural component of biomass, linear crystalline polymer of glucose held together by β-glycosidic g g y β g ylinkages strengthened by H-bonding between chains
Hemicellulose- short highly branched, less rigid and more easily hydrolyzed, amorphous polymer of 5 and 6-carbonamorphous polymer of 5 and 6-carbon sugars
Lignin- the structural component of biomass that strengthens the cell wall and cements the cells together, high
WTERT 08, New York, NY
MW, highly cross-linked aromatic
Lignin Decomposition
H2
HH2
CH4Methane producing speciesVinyl Ionic Phenoxy
LigninCH4
CH4
CH2
O
HO
CHHC
CH
CH2
CH CH
Continued Carbon enrichment
CO
O
HOHO
C
O
C
HC
CHHC
CH2
2-FuraldehydeDecarboxylation
Methylation and
WTERT 08, New York, NY
CH2
C
CH2
Lignin CharMethylation andDehydrogenationOf Lattice Structure
Cellulose DecompositionTrehalose Amylose
Levoglucosan
e a oseDehydroxylationPolymerization
(Methanol solubleOligosaccharides)
(Water solublePolysaccharides and
Furans andb l )
Furfural undergoes decarbonylationCellobiose
Carbonyls)
OO
Cellobiose
Carbonized Cellulose CharDevolatilizationNo Char formation
CH2
C
C
O
CH CHLow MW
WTERT 08, New York, NY
OCH CH
Low MWVolatilesCO,CO2,CH4,H2
Major Gasification Reactions
Water Gas Shift Steam GasificationLow Temperature High TemperatureWater Gas Shift
CO + H2O CO2 + H2
M th ti
C + H2O H2 + CO
BoudouardMethanation
C + 2H2 CH4
C + CO2 2CO
2CO + 2H2 CH4 + CO2
CO + 3H2 CH4 + H2OChar Burnout: O (Biomass/Steam)C + ½O2 CO
Steam GasificationC + H2O H2 + CO
Reverse Water Gas ShiftCO + H CO + H O
WTERT 08, New York, NY
C H2O H2 CO CO2 + H2 CO + H2O
CO Comparison
WTERT 08, New York, NY
Butterman and Castaldi, Indus. & Eng, Chem. Res, (2007) 47, 8875-8886
H2 Comparison
WTERT 08, New York, NY
Butterman and Castaldi, Indus. & Eng, Chem. Res, (2007) 47, 8875-8886
CH4 Comparison
WTERT 08, New York, NY Butterman and Castaldi, Indus. & Eng, Chem. Res, (2007) 47, 8875-8886
Value: Enhanced Char Burnout With CO2
• Identical time on stream, reaction
temperature profile, total flow rate
• Physical evidence of more efficient
gasification with COgasification with CO2Walnut Shells: 0% CO2 Walnut Shells: 30% CO2
Douglas Fir: 0% CO2
• Observed for all
Douglas Fir: 30% CO2
Poplar: 0% CO2 Poplar: 34% CO2
WTERT 08, New York, NY
• Observed for all
samples testedButterman and Castaldi, Indus. & Eng, Chem. Res, (2007) 47, 8875-8886
C C i COChar Pore Development- Enhanced Char Burnout With CO2
LigninLigninLignin Lignin
100% CO2
1oC/min
Lignin
100% CO2
1oC/min
Lignin
0% CO2 -H2O/N2
1oC/min,
WTERT 08, New York, NY
22-930oC 22-860oC 22-860oC
Cellulose/Lignin SeparationCellulose/Lignin Separation100
CO Gasification100
CO Gasification• Separation of lignin from
cellulose, CO2 processes lignin more efficiently than
70
80
90CO2 Gasification
Lignin○ 1 ° min-170
80
90CO2 Gasification
Lignin○ 1 ° min-1steam
dual
Mas
s (%
)50
60
70 ○ 1 min 1
● 100 ° min-1
dual
Mas
s (%
)50
60
70 ○ 1 min 1
● 100 ° min-1
Res
i
20
30
40
Cellulose
Res
i
20
30
40
Cellulose
200 400 6000
10▲ 1 ° min-1
Δ 100 ° min-1
200 400 6000
10▲ 1 ° min-1
Δ 100 ° min-1
WTERT 08, New York, NY
Reactor Temperature (oC)Reactor Temperature (oC)
SEM - Douglas Fir Char Fiber Enhanced i d i ifi imicropore structure during steam gasification
Increased porosity following thermalthermal treatment
WTERT 08, New York, NY
Conclusions
• Data quantitatively matches Simulation
• CO2 injection enhances CO productionT > 700oC lti i i d h b t• T > 700oC resulting in improved char burnout
• Less residual ash, especially carbon
•CO production near 400oC marks transition between the two thermal•CO production near 400 C marks transition between the two thermal degradation regimes
• 250-400oC – Local maxima of CO production• T > 700oC – Steady increase in COT 700 C Steady increase in CO
• H2 production had two regions of abrupt production • 550-575oC for herbaceous• 675-725oC for woody feedstocks
• Coal and MSW follows trends of biomass
WTERT 08, New York, NY
• CO2 accesses the recalcitrant Char more effectively than steam
AcknowledgementsgDr. Heidi Butterman – Post-Doc
Dr Eilhann Kwon PhD Student/Post DocDr. Eilhann Kwon – PhD Student/Post-Doc
Kelly Westby – Undergraduate EEE student
Professor John Dooher – Adelphi University
WTERT 08, New York, NY
Poster Session
Defining Sustainability
1 S t i bilit i th f ti i t h i th d t d
Many equate sustainability with no emissions, or minimized raw material usage, with considering the impacts at the boundaries – avoided emissions or decreased energy use
1. Sustainability is a path of continuous improvement, wherein the products and services required by society are delivered with progressively less negative impact upon the Earth – IfS:AIChE
2. Sustainability is an attempt to provide the best outcomes for the human and natural environments both now and into the indefinite future. - Wikipedia
3. Sustainable development as development that "meets the needs of the present without compromising the ability of future generations to meet their own needs". It relates to the continuity of economic, social, institutional and environmental aspects of human society, as well as the non-human environment -Brundtland Commission
Sustainability is not a way to raise taxes – NYC mayor, $8 to enter city by car during working hours
WTERT 08, New York, NY
Currently“The nature of environmental issues is changing from a regulatory to a resource focus” R. MacLean, Env. Protec. April 2003, P.12
• Education
P bli A t i f ti
g y f
• BP Re-staffing for environmental innovation
– Public Access to information
• Environment resource utilization• Walmart Supply chain vendors
“20 chemicals of concern• Home Depot Eco-Label
– Concentrators and Dilutors
• Climate change economic issue
• Carpet Recyclers profitable• GE wind power, clean water• NSF new directorate (EBW)• Venture Capital Niche
energy/environment
WTERT 08, New York, NY
Alternative EnergyAlternative Energy• The world is sensitive to energy supply (new Paradigm)
− Security, Procurement supply chain disruptions
• Two-fold increase in energy consumption (demand)• From 402 exajoules to 837-1041 over next 40 years.
• CO2 atmospheric concentrations are rising (environment)− The need for separating carbon dioxide from the product gases
and plant effluent in order to prevent it from entering the t hatmosphere.
− Space constrained or preferred land use
WTERT 08, New York, NY
• Power / heat sectors are extremely inefficient
Scale of the IssuePower / heat sectors are extremely inefficient
• ~60% of energy is wasted!• better power cycles and materials will help• All fuels are needed!
• Heat generation produces 2/3 of all CO2 emissions
• Better thermal conversion
WTERT 08, New York, NY
systems needed• Better Fuels needed!
Energy from Waste• WTE conserves fossil fuels by generating electricity. (Energy)WTE conserves fossil fuels by generating electricity. (Energy)
– 1 ton of waste combusted = 45 gallons of oil or 0.28 tons of coal– Most WTE facilities in U.S. process between 500 and 3,000 tons of waste per day– Electricity for 2.8 million homes
• WTE facilities process 14% of the MSW in the United States. (Health)– Trash-disposal needs about than 37 million people
• WTE facilities meet some of the world's most stringent standards. (Environmental, local)– Achieved compliance with new Clean Air Act pollution control standards in 2000p p– EPA data :dioxin emissions now account for less than 0.5% of dioxin emissions
• WTE facilities reduce greenhouse gas emissions. (Climate, global)– EPA estimates :WTE facilities prevent 33 million metric tons of CO2 per year avoided
WTE f iliti l t t (L d)• WTE facilities save real estate. (Land)– They reduce the space required for landfills by about 90%
• WTE is compatible with recycling. (Resource Minimization)– Communities served by WTE recycle 35% of their trash, compared to 30% for the general
population.– Annually removes more than 700,000 tons of ferrous materials– Nearly 3 million tons of WTE ash is reused as landfill cover, roadbed, or building material.
• WTE facilities provide economic benefits. (Economic)
WTERT 08, New York, NY
WTE facilities provide economic benefits. (Economic)– WTE is a $10 billion industry employs ~ 6,000 American workers annual wages ~ $400 million
Boundaries and interfaces of WTE cut across all sustainable fronts
BioenergyS i bl b l h d h i l f d k• Sustainable carbon neutral power, heat and chemical feedstocks.
• Potential to provide ~ 15% of energy demand.• Gasification
• Lower PM, NOx, and SO2, than combustion• Steam addition – Increased concentration of H2• CO2 usage – enhanced char conversion and less residue for landfill.• Provides reagents (CO & H2) for synthetic fuel/chemical production
Estimations vary widelyEstimations vary widely due to land availability and crop yields.
One piece of the alternative energy future technologies
WTERT 08, New York, NY
1.0
1.2H2 Production, basis:0.5 kmol/hr C
s/c:1.0, r:0.25
owra
te (k
g/hr
)
0.6
0.8s/c:1.0, r:0
s/c: 1.0, r:0.5
H2 F
lo
0.2
0.4
H2O/C = s/c, CO2 recyc = rCO recycle comparison for0.0
10
20
Energy Requirements
H2O/C s/c, CO2 recyc r
Energy req'd by gasifier
CO2 recycle comparison for steam to carbon ratio of 1.0.
Tradeoff: energy neutral vs
nerg
y (M
J/hr
)
-10
0
s/c:1.0, r:0
balanced by CO combustionH2 production
En
-20
10
s/c:1.0, r:0.25s/c:1.0, r:0.5
WTERT 08, New York, NY
CO Split (to combustor)
0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9-30
s/c:1.0, r:0.5
Castaldi MJ, Int J Hydrogen Energy (2007), 37, 4170 - 4179