IGSCC Mitigation Experience and Application for New Design ... · * Tests occurred at KKP-1 up to...
Transcript of IGSCC Mitigation Experience and Application for New Design ... · * Tests occurred at KKP-1 up to...
© 2016 Electric Power Research Institute, Inc. All rights reserved.
Susan GarciaEPRI – Principal Technical Leader
(with acknowledged support from Finetech: Joe Giannelli, Jeremie Varnam, Jim Tangen, Jen Jarvis and J. Sundberg)
International Light Water Reactor Materials Reliability Conference and Exhibition 2016
August 1 – 4, 2016
IGSCC Mitigation
Experience and Application
for New Design BWRs
2© 2016 Electric Power Research Institute, Inc. All rights reserved.
Optimized Water Chemistry Needed
Conditions for IGSCC & Potential Mitigating Actions
Presence of susceptible material, e.g. sensitized material, cold work, irradiation,
tensile stresses
High coolant “bad” conductivity high crack growth rates
Presence of BWR oxidants such as O2, H2O2, Cu2+, etc.
BWR operating temperature, e.g., ~ 288C
High level of oxidants high ECPs high crack growth rates
Low level of oxidants low ECPs low crack growth rates
Materials
EnvironmentStress
Reference: BWR Water Chemistry Guidelines - Volume 2 Technical Basis (3002002623)
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BWR Chemistry…a history of changes
Pure water
Hydrogen injection
Zinc addition
Noble Metal injection (NMCA)
Online Noble Metal injection
(OLNC)
Early Hydrogen injection (EHWC)
Original
Design
Operation
1983
1995
2006
2011
Chemistry control at BWRs
has changed significantly over time
0
10
20
30
40
50
200
5
200
6
200
7
200
8
200
9
201
0
201
1
201
2
201
3
201
4
201
5Nu
mb
er
of
BW
Rs
NMCA+HWC OLNC HWC (no noble metals)
What is next and what is
needed for new BWR designs?
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Electrochemical Corrosion Potential (ECP)
IGSCC Initiation “Threshold” = -230
mV(SHE)
0 0.1 0.2 0.3 0.4 0.5 0.6
-600
-500
-400
-300
-200
-100
0
100
200
Conductivity (µS/cm)
Elec
troc
hem
ica
l Pot
entia
l (V
, SH
E)
No IGSCC
IGSCC
BWR Data Sources Dresden 2 FitzPatrick Ringhals 1 Nuclenor Hatch 1 Hope Creek NMP 1
IGSCC
NO IGSCC
Pure
Water
EC
P,
mv(S
HE
)
Goal: maintain < -230 mV(SHE) ECP values
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Stress Corrosion Cracking Mitigation with Hydrogen Water
Chemistry (HWC)
1.4 x 10-7 mm/s
<4 x 10-9 mm/s
<4 x 10-9 mm/s
Crack Growth Rate studies show significant reductions with HWC
Reference: BWR Water Chemistry Guidelines - Volume 2 Technical Basis (3002002623)
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STEAM
FEEDWATER
HIGH PRESSURE TURBINE
LOW PRES TURBINE
GENERATOR
Feedwater Hydrogen Concentration (PPM)
Normalized Main Steam Line Activity
H2 Addition to Feedwater (HWC)
Mitigates IGSCC, but Main Steam
Dose Rate increases
Due to N-16
Area Dose
Rate
Increase
HWC Side Effects and
Benefits of NMCA/OLNC
HWC Operating
Regime
NC/OLNC Operating Regime
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On-Line NobleChem™ (OLNC)
Platinum catalyzes recombination reactions between hydrogen and oxidants
Criteria:
– Requires a molar ratio of hydrogen to oxidants ≥2 (oxygen equivalent) at the most limiting location at which mitigation is targeted. For conservativism, many plants target molar ratios of ≥ 3 or ≥ 4
– Requires sufficient noble metal coverage on the surfaces
Less hydrogen required, typically 0.15-0.4 ppm feedwater hydrogen so MSLRM dose rates remain low
Mitigation is not claimed in:
– boiling regions (cannot achieve required molar ratio)
– the upper downcomer - incomplete mixing between feedwater and discharge from the steam separators is assumed
Significant BWR operating experience demonstrating effectiveness
Reference: BWRVIP-99-A Crack Growth Rates in Irradiated Stainless Steels in BWR Internal Components (1016566)
8© 2016 Electric Power Research Institute, Inc. All rights reserved.
BWR Internals Mitigation with HWC and Noble Metals
NM
CA
pro
tect
ed re
gion
s
HW
C p
rote
cted
regi
ons
HWC-Moderate
• ECP reduction in the upper shroud annulus as gamma from the core
recombines H2 and O2
• ECP reduction depends on H2
injection amount
• Typically <-230 mV(SHE) around upper jet pump
• Hydrogen injection rates are >1ppm
Noble Metals + HWC
Noble metals (Pt alone or Pt+Rh)
needed on wetted surfaces
ECP reduction achieved as soon
as feedwater and separator/dryer
return flow are fully mixed to create
>2:1 H2 to oxidant molar ratio
Additional areas of protection with
NMCA – upper, outer shroud
regions (red region)
Hydrogen injection rate is <0.3 ppm
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BWR-4 ECP Response following 2 OLNC Applications
2 Pt reference electrodes in modified
LPRM string (lower plenum)
OLNC Applications
– August 6, 2014 and July 24, 2015
Increase in ECP from -490 mV(SHE) to
~380 mV(SHE) after 1st OLNC
Reduction in ECP from ~-380 mV(SHE)
to ~-490 mV(SHE) during 2nd OLNC
Following 2nd application, gradual
increase in ECP values, similar to
experience after 1st OLNC application
ECP values recovering after November
2015 mid-cycle outage to repair
recirculation pump seal
Mid
-Cycle
Ou
tag
e
HWC-M
-550
-500
-450
-400
-350
-300
-250
5/1/2014 10/28/2014 4/26/2015 10/23/2015
Ele
ctr
och
em
ical
Co
rro
sio
n P
ote
nti
al, m
V(S
HE
)Pt-1 Pt-2 OLNC
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Return to moderate HWC
– One U.S. BWR-2 has returned to M-HWC
2 NMCA applications (2003 and 2009)
Economic decision to not apply OLNC (plant to shutdown in 2019)
Earlier OLNC
– Original guidance to apply 90 days after startup (fuel concerns)
– Reduced to 60 days with fuel vendor concurrence
– Evaluating 30 day application hold period
– Swiss BWR will be the first to apply sooner, and has applied several mini-applications in place of annual applications
Methanol Injection
– Applied at German BWR in 2003/2004 at full power
– Startup application at U.S. BWR in March 2016 (data evaluation indicates mitigation not achieved)
TiO2 Injection
– Applied at Japanese BWR in 2010 (plant shutdown in 2011)
– Being considered at U.S. BWR that will shutdown in 2019
Mitigation Technologies – Recent Changes
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How Does OLNC Mitigation Experience Apply to
New Design BWRs?
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Comparison of Reactor Vessels
Extended
Chimney
Active Fuel
height is shorter
Taller
Downcomer
External
Recirculation loop
No external recirc.
loop
BWR 3-6 ABWR ESBWR
No external recirc. loop;
natural circulation
Jet pumps
10
RIP
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Comparison of Design Parameters Affecting Radiolysis
Property BWR 6 ABWR ESBWR
Core Thermal Power (MWt) 3579 3926 4500
Core coolant flow rate (kg/s) 13104 145028763-
10376
Feedwater flow rate (kg/s) 1936 2118 2451
Max. Exit void fraction within
assembly0.79 0.751 0.9
Core average void fraction in active
coolant0.414 0.408 0.53
Core average inlet velocity (m/s) 2.13 1.96 1.12
Max. core inlet velocity (m/s) 2.6 2.29 1.15
Active Fuel Height (m) 3.7 3.7 3.0
RPV Diameter (m) 6.4 7.1 7.1
RPV Height (m) 21.8 21.1 27.7
Higher void
fraction
FW to Core
flow rate
higher
0.24 - 0.28 vs.
0.14
Shorter
active fuel
Larger radius
and taller RPV
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Void Fraction in Average Channel of the ESBWR and ABWR
[Data from Ch 4 ABWR Design Control Doc. Rev. 4, Ch 4 ESBWR DCD Rev 10, and BWRVIA]
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
0.0 0.5 1.0 1.5 2.0 2.5 3.0 3.5 4.0
Vo
id f
racti
on
Axial Height from bottom of Active Fuel (m)
ABWR ESBWR BWR6
Bulk boiling in
ESBWR starts at
a lower elevation
ESBWR Core is
shorter, and exit
void fraction is
higher
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Summary of IGSCC Mitigation OptionsTechnology Type of Method Operating
Experience?
Increase in
MSLR Dose?
Other Notes, Requirements, Limitations
NWC (Non-additive) - - Yes -More frequent monitoring, careful control of
water chemistry required
HWC-Moderate x Yes Yes Volatile
NobleChem™/OLNC +
Low HWCx x Yes Minimal Volatile
Hydrazine or
Carbohydrazidex No
Decomposes at operating temperatures
(applicable to startup only)
Methanol x Limited*Likely,
if used alone
Volatile, less than H2
Kinetics of methanol-oxidant reactions may be
slow; UV light may be required to catalyze
TiO2 x Limited **
Does not require H2 if there is sufficient UV
light at the surface (small amount of H2 needed
for regions with insufficient UV) Compatibility
with noble metal treatment, methanol, and
depleted zinc oxide (DZO) is not known
* Tests occurred at KKP-1 up to 0.8 ppm FW injection during full power operation and LAS1 during startup. (both insufficient for IGSCC mitigation)
** Application and partial cycle operation at 2F-1. No ECP measurements.
16© 2016 Electric Power Research Institute, Inc. All rights reserved.
IGSCC Considerations for Advanced BWR Designs
ABWR
– Hydrogen mini-tests and radiolysis modeling indicate that the response to hydrogen is similar for ABWRs and BWR 2-6:
Regions/components mitigated and amount of feedwater hydrogen required will be very similar.
ESBWR
– Radiolysis and water chemistry have not been modeled.
– Significantly more boiling than BWR 2-6 and ABWR. Core is shorter, downcomer is longer.
Hydrogen may not be as effective
Extended chimney piece above core (may be difficult to mitigate)
Longer downcomer, with shorter active core height, may lead to less exposure to high gamma rates to encourage recombination.
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Hydrogen Water Chemistry and Noble Metal Treatments
Hydrogen Mini-Test at K7 and radiolysis models suggest that the ABWR responds
similarly to hydrogen injection as BWR 2-6.
Molar ratios in Lungmen ABWR
calculated with DEMACE
radiolysis code
-0.7
1.3
3.3
5.3
7.3
9.3
0.0 0.2 0.4 0.6 0.8 1.0 1.2 1.4 1.6 1.8 2.0
Hyd
rog
en
: O
xid
an
ts M
ola
r R
ati
o
FFW H2 (ppm)
Upper Plenum Outlet
Top DC
Downcomer Outlet
Reactor Internal Pump Outlet
Bottom Lower Plenum Outlet
Molar ratios in an ABWR
calculated with BWRVIA[BWRVIA Modeling of Advanced Boiling Water Reactor. EPRI, Palo Alto, CA: 2011. 1023003]
[M. Wang, T.K. Yeh, Nucl. Sci. Eng. 180 (2015) 335–340]
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Hydrogen Water Chemistry and Noble Metal Treatments
MSLR dose rate increase at K-7 with feedwater hydrogen-
increase is similar to those at BWR 2-6.
0
1
2
3
4
5
6
0.0 0.5 1.0 1.5 2.0 2.5
Main
Ste
am
Lin
e D
os
e R
ate
In
cre
ase
Feedwater DH (ppm)
OLNC+HWCModerate HWC
[Murai et al. 7th Int. Conf. Nucl. Eng., JSME, Tokyo, Japan, 1999]
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Alternate Mitigation Technologies for ABWR Application
Limited BWR experience with Methanol or TiO2 but no ABWR experience
Hydrogen response is similar for the ABWR and BWR 2-6. It is likely that
methanol in an ABWR would be similar to that in a BWR 2-6.
– Tests with Methanol alone indicate it may take high concentrations
May be better when used with NMCA/OLNC.
– TiO2 could offer mitigation in more of the reactor vessel (upper plenum, upper
downcomer, etc.).
Dependent on coverage, UV intensity. Because the reactor vessel design is
different (RIP vs. jet pumps and recirculation loop), the required surface
loading in the downcomer may be different from that for a BWR 2-6. No
recirculation loop to mitigate.
Radiation Field Dose Rates: It is not known if methanol or TiO2 can produce the
very low ECP (-500 mV(SHE)) which is beneficial for dose rates due to incorporation
of activated corrosion products in oxide layers (when used with DZO).
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Alternate Mitigation Technologies for ESBWR Application
Methanol: may provide some advantage over hydrogen
– Less volatile than hydrogen. However, methanol has not yet been proven to
mitigate IGSCC in BWRs, demonstrations had limited monitoring.
TiO2: since all of the vessel cannot be mitigated with HWC-M or NMCA/OLNC-
HWC, TiO2 may be useful for mitigation in oxidizing regions (top of the
downcomer, chimney, upper plenum, etc.).
Other considerations: would it be better to design the ESBWR chimney piece to
avoid IGSCC, or plan on replacing it (material selection, manufacturing)?
Summary:
IGSSC mitigation experience with BWR 2-6 designs may be applicable to ABWRs
Further radiolysis and water chemistry modelling required for ESBWRs
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