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Coal Syngas Testing at NETL
Energy Systems Dynamics Division
2008 SECA WorkshopAugust 5-7, 2008Randall GemmenKirk GerdesGreg Hacket
National Energy Technology Laboratory
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2K-2571
Goal
Identify the effects of trace coal syngas species on SOFC anodes, and identify the trace material exposure levels
that will be acceptable to fuel cell operation.
At present, no data exist to guide developers on how to design At present, no data exist to guide developers on how to design coal syngas cleanup systems suitable for SOFC operationcoal syngas cleanup systems suitable for SOFC operation
Trace elements:
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2K-2571
Effect of Trace Species on SOFC Anode
• Affect the ability of Ni to promote the electrochemical reactions− Trace species on Ni surface inhibit the adsorption of
H2, CO, or dissociation of H2• Affect the ability of YSZ to transport oxygen ion
− Formation of secondary zirconia phases • Affect the electrical conductivity
− Formation of secondary nickel phases such as nickel-phosphide
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2K-2571
Questions
• What is the variability of trace elements in coal?• What is the effect of different gasification
technology on the potential for anode attack?• Aside from trace metal species, are other
‘contaminants’ (e.g., tars) important to consider?• Is individual contaminant testing representative
of actual coal syngas operation?
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2K-2571
Outline
• Analysis−Assess the contaminants in variety of coals− Identify potential sensitivities of gasification design
on trace species attack• Experimental
− Individual trace specie evaluations−Direct coal syngas testing
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2K-2571
Advanced Coal Based IGFC System
ASU
GasCleaning
air
N2
coal
SOFC Anode
SOFC Cathode
air
Pressurized SOFC Oxy-Comb
HeatRecovery
oxygen
CO2Condenser
CO2 Compressor& dryer
oxy-comb O2
stackgas
expander
expander
Gasification
Water Recycle
compressor
EnhancedOil Recovery
Deep SalineAquifer
UnmineableCoal Beds Depleted Oil & GasReservoirs
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2K-2571
Trace Metal Contaminants(Coal-Type Dependency)
• USGS analysis of trace elements in coals.
• Different coals have different levels of given a given contaminant.
• Data given here shows deviations (from average) approach 140%.
0
10
20
30
40
50
60
70
As Cr Ni Co Sb Pb Cd Zn Be Mn Th UTrace Element
Con
cent
ratio
n in
Coa
l [m
olar
ppm
]
WyodakElkhorn/HazardPittsburghIllinois #6
Ref. USGS, 1998
0%
20%
40%
60%
80%
100%
120%
140%
160%
As Cr Ni Co Sb Pb Cd Zn Be Mn Th U
Trace Contaminant
Stan
dard
Dev
iatio
n [%
of A
vera
ge V
alue
]
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2K-2571
1 ATM/700oC
1 ATM/900oC
1
1—Swartz Pumpe2—Exxon Singapore3—Tampa4—El Dorado5—Fife6—Pernis & KBR7—Valero-Delaware8—Eastman & PSI 9—Sarlux10—ILVA11—Catalytic12--KRW
23
7
8
46
9
10
1 ATM/800oC
5
11
12
Gasification Dependencies
0%
20%
40%
60%
80%
100%
Schw
artz P
umpe
Exxo
n Sing
apor
eTa
mpa
El Do
rado
Fife
Pern
isKB
R
Valer
o-Dela
ware
KRW
Eastm
an PSI
Entra
ined*
Sarlu
xILV
A
Catal
ytic G
asifie
rCum
ulat
ive
Mol
e Pe
rcen
t [%
]
H2
CO2
CO
H2O
N2
CH
4
Ref.: Jones and Schilling (2002) (*Trembly et al., 2007)
0.0%0.2%0.4%0.6%0.8%1.0%1.2%1.4%1.6%1.8%
Catal
ytic
Schw
artz
Fife
ILVA PS
IEn
traine
dSa
rlux
Exxo
nKR
WTa
mpa
El Do
rado
Eastm
anPe
rnis
KBRPe
rcen
t Ni R
eact
ed in
400
Hr [
%]
C(s)
Trembly et al. (2007)
Contaminant Loading from Trembly et al. (2007)
0
0.2
0.4
0.6
0.8
1
1.2
Catal
ytic
Schw
artz
Fife
ILVA PS
IEn
traine
dSa
rlux
Exxo
nKR
WTa
mpa
El Do
rado
Eastm
anPe
rnis
KBR
Frac
tion
Syng
as C
onta
min
ant
Rea
cted
With
Ni [
1]
Sb
P
As
(Warm Gas Cleanup = 400 oC; Cell Temperature = 800 oC; 1atm; FU=const.; 400 Hr Run)
(anode inlet conditions)
(anode inlet conditions)
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Gasification Tars• Gasifier syngas consists of tars in addition to H2, CO, CO2, H2O, char, and volatile trace material.• A typical tar yield is about 3–4%, by weight, of the coal
charged (Menéndez and others, 2000).• Coal tar elemental analysis: 80% C, 6% H, 1% N, 3% S, 10%
O.• Benzene soluble tar components by volume:
− Benzenes (3%), Naphthalenes (15%), Aromatics (12%), Acenaphthenes (12%), Fluorenes (9%), Indenes (5%), Dibenzofurans (6%), Phenylnaphthalenes (7%), Others (31) (Bureau of Mines (1974))
• Tars = All organic components having molecular weight higher than benzene. (Bergman et al. 2002).
• Major factors affecting tar composition are the temperature profile, gasifying agent, partial pressure of hydrogen, the residence time of the coal in the gasifier, and coal structure (Miller et al. 1980).
• Syngas treatment: − Filters and scrubbers− Cool syngas to below 100 to 260 oC to remove tars. (e.g., U.S. Patent 4198212)− Catalytic reaction beds
• Short term exposures (ca. 20 hrs) of Ni/GDC anode to tar from bio-fuel gasifier result in no carbon or fuel cell performance changes. (Hofmann et al. 2008)
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Outline
• Analysis−Assess the contaminants in variety of coals− Identify potential interactions between trace species
and anode across a variety of gasification systems• Experimental
−Perform individual trace specie evaluations• H2Se and Benzene
−Perform direct coal syngas testing
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2K-2571
Methodology to Identify Cleanup Target Levels
• Single trace material testing is used to assess impact of specific species− Attack on active sites at the electrochemical TPB (relatively short time constant)− Attack on SOFC material to generate resistive secondary phase (relatively large time
constant)− Other … ?
0.00
0.03
0.06
0.09
0.12
1.E-05 1.E-03 1.E-01 1.E+01
• Method of attack characterized by V(t) and post test analysis (XRD, SEM, EDS) from test data:− 0.1 ppm, 1 ppm, 10 ppm
• Rates extrapolated to ‘zero-effect’level (continually refined as more data is available!)
• Avoid time and expense required to experimentally show “zero-effect”
Extrapolated range Tested range
hrs
days
mos
yrs
decs
Acceptable degradationZero-effect
Trace Material Concentration PPM
Deg
rada
tion
[%/1
000
hour
s]
http://theodoregray.com/PeriodicTable/Samples/033.5/index.s12.html
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900 °C
700 °C
Experimental Methodology
• Anode supported SOFCs with Ni/YSZ anodes operated between 750-800ºC
• Cells operated with simulated coal syngas containing single trace species of interest
• VI scans and EIS methods used during testing• Post trial SEM, EDS, and XRD used
Ca—Pt Mesh/Paste; An—Ni Mesh/Paste
PermeationTube
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Results: H2Se Testing
SOFC VoltageOperating at 800 °C at 0.25 Acm-2 Over Time with 5 ppm H2Se
0
0.2
0.4
0.6
0.8
1
1.2
0 50 100 150 200 250Time [hr]
Cel
l Vol
tage
[V]
Initial H2Conditioning
Start Pure Syngas Injection
Start 5ppm H2Se Injection
Return to H2
Return toPure Syngas
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2K-2571
“Light Tar” Test
No visual carbon was observed on cell after test.No significant carbon was measured via XPS.
0.000
0.200
0.400
0.600
0.800
1.000
1.200
0.0 100.0 200.0 300.0 400.0 500.0 600.0Time (h)
Cel
l Vol
tage
[V] /
Cur
rent
[A]
Condition on 97% H2/H2OStart of Syngas + 150 ppm benzene
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SOFC Operation on Direct Syngas
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PSDF Process Flow Diagram
Gas Analysis
MCA Test Rig
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Test RigMulti-cell Array
• Permits parallel operation of 12 button cells
• Divided into 4 channels of 3 cells each• Improves testing method
− Rapid collection of repeat data− Reduces systematic experimental error
• Reduces sources of contamination− Seals− Materials
• Status− Field test started on Mississippi lignite
coal.
2
2
2
4
4
4
5
5
5
2
2
2
4
4
4
5
5
5
2
2
2
4
4
4
5
5
5
2
2
2
4
4
4
5
5
5
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Gas Analysis—Mercury
m/z 195 197 199 201 203 205
25
Hg
m/z 195 197 199 201 203 205
25
Hg
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Gas Analysis—Cadmium
m/z 108 109 110 111 112 113 114 115 116 117 118 119
5000 Cd
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Gas Analysis—Selenium
m/z 75 76 77 78 79 80 81 82 83 84 85 86
50
Se
m/z 75 76 77 78 79 80 81 82 83 84 85 86
50
Se
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Gas Analysis—Phosphorus
Phosphorus
0.E+005.E+061.E+072.E+072.E+073.E+073.E+074.E+074.E+075.E+07
0 20 40 60 80Time [sec]
Cou
nts
per s
econ
d
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Gas Analysis—Mercury
Hg 198-204
0
100
200
300
400
500
600
700
0 50 100 150 200Time [sec]
Cou
nts
per s
econ
d
Hg 198Hg 199Hg 200Hg 201Hg 202Hg 204
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Cell Conditioning on Hydrogen(92% H2/H2O)
Cell 6
0
0.2
0.4
0.6
0.8
1
1.2
0.00 20.00 40.00 60.00 80.00Time [hr]
Cel
l Vol
tage
[V]
Cel
l Cur
rent
[am
p]
V
I
Cell 5
0
0.2
0.4
0.6
0.8
1
1.2
0.00 20.00 40.00 60.00 80.00Time [hr]
Cel
l Vol
tage
[V]
Cel
l Cur
rent
[am
p]
V
I
Cell 2
0
0.2
0.4
0.6
0.8
1
1.2
0.00 20.00 40.00 60.00 80.00Time [hr]
Cel
l Vol
tage
[V]
Cel
l Cur
rent
[am
p]
V
I
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2K-2571
Syngas Started
Cell 4 / OCV
0
0.2
0.4
0.6
0.8
1
1.2
0 10 20 30 40Time [hr]
Cel
l Vol
tage
[V]
Cell 6 / 0.05 A/cm2
0
0.2
0.4
0.6
0.8
1
1.2
0 10 20 30 40Time [hr]
Cel
l Vol
tage
[V]
0123456789
0 10 20 30 40Time [hr]
Gas
Flo
w [S
LPM
]
Air
H2 Syngas
•Planned end date for syngas run is mid August.•Post test analysis--Cells will be examined using a variety of micro analytical techniques to assess possible trace material effects.
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Trace Coal Species Summary
• Some variability of trace metals due to coal types—this will need to be accounted for in cleanup design.
• Tars may be present for low temperature gasifiers, but no negative impact has been shown yet—suggest further studies on higher MW compounds.
• Continuing individual coal trace species studies to determine impact on fuel cell performance
• Awaiting completion of SOFC operation on direct syngas to assess actual effect of operating on coal syngas
• Our work and work of other labs will be brought together in the future to give clear cleanup target levels
Programmatic driver: Quantification of cleanup target levels for trace materials
in coal syngas delivered to SOFC
Coal Syngas Testing at NETLGoalEffect of Trace Species on SOFC AnodeQuestionsOutlineAdvanced Coal Based IGFC SystemTrace Metal Contaminants�(Coal-Type Dependency)Gasification DependenciesGasification TarsOutlineMethodology to Identify Cleanup Target LevelsExperimental MethodologyResults: H2Se Testing“Light Tar” TestSOFC Operation on Direct SyngasPSDF Process Flow DiagramTest Rig�Multi-cell ArrayGas Analysis—MercuryGas Analysis—CadmiumGas Analysis—SeleniumGas Analysis—PhosphorusGas Analysis—MercuryCell Conditioning on Hydrogen�(92% H2/H2O)Syngas StartedTrace Coal Species Summary