mercury control in the boiler -...
TRANSCRIPT
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Mercury Control in
the Boiler
Connie Senior
Reinhold NOx Roundtable
Columbus, Ohio
February 13-14, 2012
ADA: Innovate, Develop, Commercialize
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Motivation for This Presentation
• There’s more than activated carbon, when it
comes to mercury control in coal-fired boilers
• Chemistry of mercury in the boiler and the
interaction of mercury with other control
processes, like SCR, affect the performance of
downstream mercury control from activated
carbon injection or scrubbers
• Topics to be discussed: control of unburned
carbon, halogen injection, impact of SCRs
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Hg Removal in the Boiler
• Hg isn’t removed in the boiler
• But, some things that happen in the boiler affect
how much mercury can be removed
downstream
• How is Hg removed?
• Adsorption on particles (fly ash, sorbents) and
removal in the particulate control device
• Absorption of oxidized mercury in scrubbers
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Adsorption
• How do we get more mercury onto particles?
0%
20%
40%
60%
80%
100%
10 100 1,000 10,000
%H
gp
at
PC
D I
nle
t
Coal Chlorine, ppm dry
Cold-side ESP & FF
Hot-side ESP
• More halogens
generally mean
more particulate
Hg
Source: 1999 ICR Data
• Other factors:
• Type of PCD
• SO3
• Unburned
carbon in ash
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Unburned Carbon & ESPs
• Data from
bituminous
coals in pc-
fired boilers
0%
20%
40%
60%
80%
100%
0% 10% 20% 30%
Hg
Re
mo
val
acro
ss P
CD
Loss-on-ignition (LOI) in fly ash, wt%
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Unburned Carbon & Fabric Filter
• T-fired boiler with
low-NOx
combustion
system, low-sulfur
fuel
• Unburned carbon
changed by
changing
combustion
parameters
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
4 6 8
Hg
Re
mo
val
acro
ss F
F
Unburned carbon in ash, wt%
Total Hg
Gaseous Hg
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Absorption
• How do we get more Hg into the scrubber?
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
0% 20% 40% 60% 80% 100%
Re
mo
va
l of
Hg
acro
ss F
GD
Fraction Hg2+ at Inlet
Dry FGD, FF
Wet FGD
• Higher fraction of
oxidized Hg at
scrubber inlet =>
higher Hg
removal
• Factors:
• Halogen in fuel
• Re-emission of
Hg0 in wet FGD
Source: NETL, EPRI demos
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Why Add Halogens?
• Adding halogens to fuel or flue gas:
– Halogen content of US coals varies widely
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http://ugs.utah.gov/emp/mercury/index.htm
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Why Add Halogens?
• Adding halogens to fuel or flue gas:
– Halogen content of US coals varies widely
• Bromine content typically 1% to 4% of chlorine content
Source: USGS COALQUAL database
y = 0.0482xR² = 0.1319
0
10
20
30
40
50
60
0 50 100 150 200 250 300
Br,
ug/
g
Cl, ug/g
Eastern Interior (Illinois Basin)
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Why Add Halogens?
• Adding halogens to fuel or flue gas:
– 500 ug/g Cl in coal = ~40 ppmv HCl in flue gas
– 500 ug/g Br in coal = ~17 ppmv HBr in flue gas
0
20
40
60
80
100
0 200 400 600 800 1,000
HX
in g
as,
pp
mv,
3%
O2
dry
Halogen in Coal, µg/g dry
HCl
HBr
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Why Add Halogens?
• Adding halogens to
fuel or flue gas:
– Halogen content of
US coals varies
widely
– Oxidation of Hg and
capture of Hg on fly
ash enhanced with
additions of
halogens, like Cl and
Br
0
20
40
60
80
100
0 500 1000 1500 2000 2500 3000
Halogen in Coal, ppmw dry
%O
xid
ize
d H
g a
t A
ir P
reh
ea
ter
Ou
tle
t
NaCl
MgCl2
CaCl2
HCl
CaBr2
Halogen addition at various
full-scale PRB boilers
Source: Dombrowski et al., 2006
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Why Add Halogens?
• Adding halogens to
fuel or flue gas:
– Halogen content of US
coals varies widely
– Oxidation of Hg and
capture of Hg on fly
ash enhanced with
additions of halogens,
like Cl and Br
– Many plants’ APCDs
can take advantage of
native capture
Source: 1999 ICR
0%
20%
40%
60%
80%
100%
10 100 1,000 10,000
Hg
Re
mo
va
l a
cro
ss F
GD
Coal Chlorine, ppm dry
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Summary: Why Add Halogens?
• Adding halogens to fuel or flue gas:
– Halogen content of US coals varies widely
– Oxidation of Hg and capture of Hg on fly ash
enhanced with additions of halogens, like Cl and Br
– Many plants’ APCDs can take advantage of native
capture
• Adding halogens to activated carbon increases
the ability to capture elemental Hg in low-
halogen flue gas
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How Effective Are Halogens?
• Halogens increase
oxidized mercury:
Br more effective
than Cl (on an
equal mass basis)
• Increased Hg
removal across
scrubbers
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
1 10 100 1000 10000
Tota
l Hg R
em
oval (c
oal-
to-s
tack)
Halogen in coal, ug/g
Chlorine addition
Bromine injection
Monticello: PRB/lignite,
ESP, wet FGD
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How Effective Are Halogens?
• Halogens increase
oxidized mercury:
Br more effective
than Cl (on an
equal mass basis)
• Increased Hg
removal across
scrubbers
• Halogens increase
effectiveness of
PAC Source: DOE/EPRI sampling campaigns
0
20
40
60
80
100
0% 20% 40% 60%
Hg
Rem
ova
l
Percent recommended KNX rate
KNX
KNX + 0.14 lb/MMacf PAC
Plant Hardin: SCR/SDA/FF
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Effect of SCRs on Added Halogens
• Catalysts drive reactions toward equilibrium
– Results will be catalyst-specific
• Adding Br to the fuel makes the shift to Hg2+ take
place at higher temperatures (than Cl)
0%
20%
40%
60%
80%
100%
600 700 800 900
%O
xid
ized
Hg
Temperature, oF
Baseline+ 3 ug/g Br+ 18 ug/g Br+ 33 ug/g Br+ 328 ug/g Br
Equilibrium
modeling of
Plant Miller data
of Berry et al.
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Effect of SCRs on Added Halogens
• Catalysts drive reactions toward equilibrium
– Results will be catalyst-specific
• Adding Br to the fuel makes the shift to Hg2+ take
place at higher temperatures (than Cl)
Comparison of
Plant Miller data
of Berry et al.
with calculated
equilibrium
0
1
2
3
4
5
6
7
8
9
0 100 200 300 400
Hg0 ,
ug
/dN
m3
Added Br, ug/g coal equivalent
SCR Inlet
SCR Outlet
Equilibrium
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Effect of SCRs on Added Halogens
• Bromine is more
efficient (equal
mass basis) than
chlorine at
oxidizing Hg
across SCRs
– Results will be
catalyst-specific
– Subbituminous
(low-chlorine)
coals only
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
4.0
4.5
0 100 200 300 400
Hg0
, ug
/dN
m3
Halogen, ug/g coal equivalent
Bromine
Chlorine
Equilibrium at 720oF
Subbituminous Coals
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Fate and Impacts of Halogens
• What are the potential impacts of halogen
addition on the boiler, APCDs, and emissions?
– Corrosion
– Fly ash
– Stack emissions
– Scrubber interactions
Boiler
Burners
Air Heater
Fuel
Coal Pulverization
Coal Supply
Particulate Collector
SO 2 Scrubber
Induced Draft Fan
Stack
SCR
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Corrosion in Flue Gas
• Indirect evidence that HBr
might be more corrosive
than HCl at flue gas
temperature
• No direct comparison, but
HBr corrosion higher than
baseline (no HBr) in
simulated flue gas
(6-month study)
0
0.02
0.04
0.06
0.08
0.1
0.12
0 100 200 300 400
Co
rro
sio
n l
oss
, m
m
Temperature, oF
Baseline
51 ppmv HBr
• Chlorine corrosion in furnaces can occur for very
high levels of chlorine in coal (> 2000 µg/g)
– Bromine addition at much lower concentrations
Zhuang et al., 2009
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Bromine Addition: Fly Ash Impacts
• Bromine additive or brominated PAC results in
increase in Br in fly ash
• Example: Br injection at Monticello (C-ESP)
0
50
100
150
200
250
300
350
0
1
2
3
4
5
6
7
8
11/1/05 11/15/05 11/29/05 12/13/05
Br
add
ed
m µ
g/g
co
al
Br,
µg
/g
Br in fly ash Br injected
Bromine injection at Monticello (EERC, URS data)
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Bromine Addition: Fly Ash Impacts
• Bromine additive or brominated PAC results in
increase in Br in fly ash
• Example: Br injection at Plant Miller (PRB, C-ESP)
• According to the authors:
• Hg concentration in fly ash
didn't increase with Br
injection
• 1% of Br captured by fly ash
• 50% of Br on fly ash leached
in SPLP test
0.0
0.1
0.2
0.3
0.4
0
2
4
6
8
10
12
14
0 20 40 60
Leac
hat
e, m
g/L
Fly
Ash
, µ
g/g
Added Br, µg/g coal equivalent
Br in Fly Ash
Br in Leachate
Dombrowski et al., 2008
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Source: 2010 ICR
Chlorine Emission from APCDs
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Meramec
PIPP FF
C-ESP
Brominated
PAC injection
All boilers are pulverized coal, burning subbituminous coal
Bromine Emission from APCDs
0% 50% 100%
Boiler 3
Boiler 2
Boiler 1
Percent of added halogen emitted in stack
C-ESP
C-ESP
C-ESP
Fuel
addition
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Source: 2010 ICR
Chlorine Emission from APCDs
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Halogens in Wet Scrubbers
• Adding halogens (Cl or Br) increases oxidized Hg,
which increases capture of Hg in scrubber
• Wet FGD scrubbers remove halogens efficiently
– Average Cl removals for wet FGDs (2010 ICR): 81% for
subbituminous, 97% for bituminous
– Removal of Br at Plant Miller wet FGD: 94-96%
(Dombrowski et al., 2008)
• Halogens build up in wet scrubber liquor
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Halogens in Wet Scrubbers
• Halogens and Hg build up in wet scrubber
liquor… slowly, depending on scrubber design
Bromine injection at Monticello (EERC, URS data)
0
50
100
150
200
250
300
350
0
100
200
300
400
500
11/1/05 11/15/05 11/29/05 12/13/05
Br
add
ed
m µ
g/g
co
al
Br,
mg
/L, H
g, µ
g/L
Br in FGD liquor Hg in FGD liquor Br injected
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Halogens and Wet Scrubbers
• Increased Cl, Br concentration in scrubber liquor
can decrease Hg re-emission
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Halogens and Wet Scrubbers
Data from bituminous site with C-ESP, wet FGD
Se in fly
ash, µg/g
% Se capture
by fly ash
Se in FGD
liquor, µg/L
Baseline 24 70% 300
Br addition 10 20% 4900
(Dombrowski et al., 2011)
• Recent observations (Air Quality VIII) that Br
addition to the fuel increases Se in scrubber liquor
– Less uptake of Se by fly ash means more Se enters
FGD
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Halogens Summary
Fly
Ash
Boiler
Burners
Air Heater
Fuel
Coal Pulverization
Coal Supply
Particulate Collector
SO 2 Scrubber
Induced Draft Fan
Stack
SCR
Scrubber
Blowdown
Stack
Emission Halogen
Injection
Halogenated
Carbon
Injection
• Halogen fuel/flue gas additives OR halogenated PAC
• Where do halogens go?
• Some removal in
particulate control
devices
• Efficient removal in FGDs
• Br is “new kid on the
block” – information
needed:
• Corrosion
• Multi-media fate
• Trace metal interactions
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Hg Removal in the Boiler
• How is Hg removed?
• Adsorption on particles (fly ash, sorbents) and
removal in the particulate control device
• Absorption of oxidized mercury in scrubbers
• How can we improve removal by what happens
in the boiler?
• Increase unburned carbon – if you can
• Consider adding more halogens if
• There’s enough LOI, but halogens are low
• There’s a scrubber
• Keep SO3 low post-APH
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