ML062540237: Difference between revisions

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| issue date = 09/27/2006
| issue date = 09/27/2006
| title = License Amendments 233 and 229 Revised Storage Criteria for Low-enriched Uranium Fuel
| title = License Amendments 233 and 229 Revised Storage Criteria for Low-enriched Uranium Fuel
| author name = Stang J F
| author name = Stang J
| author affiliation = NRC/NRR/ADRO/DORL/LPLII-1
| author affiliation = NRC/NRR/ADRO/DORL/LPLII-1
| addressee name = Jamil D
| addressee name = Jamil D
Line 9: Line 9:
| docket = 05000413, 05000414
| docket = 05000413, 05000414
| license number = NPF-035, NPF-052
| license number = NPF-035, NPF-052
| contact person = Stang J F, NRR/DORL, 415-1345
| contact person = Stang J, NRR/DORL, 415-1345
| case reference number = TAC MC8439, TAC MC8440
| case reference number = TAC MC8439, TAC MC8440
| document type = Letter, License-Operating (New/Renewal/Amendments) DKT 50, Safety Evaluation
| document type = Letter, License-Operating (New/Renewal/Amendments) DKT 50, Safety Evaluation
| page count = 25
| page count = 25
| project = TAC:MC8439, TAC:MC8440
| project = TAC:MC8439, TAC:MC8440
| stage = Other
| stage = Acceptance Review
}}
}}


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==Enclosures:==
==Enclosures:==
: 1. Amendment No. 233 to NPF-35  
: 1. Amendment No. 233 to NPF-35
: 2. Amendment No. 229 to NPF-52  
: 2. Amendment No. 229 to NPF-52
: 3. Safety Evaluationcc w/encls:  See next page September 27, 2006Mr. Dhiaa Jamil Vice President Catawba Nuclear Station Duke Power Company LLC 4800 Concord Road York, SC  29745
: 3. Safety Evaluationcc w/encls:  See next page September 27, 2006Mr. Dhiaa Jamil Vice President Catawba Nuclear Station Duke Power Company LLC 4800 Concord Road York, SC  29745


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Catawba 1 and 2 currently complies with a design basis that requires preventing criticality in a spent fuel pool based on the K eff of the SFP storage racks loaded with fuel of the maximum fuelassembly reactivity not exceeding 0.95, at 95-percent probability, 95-percent confidence level, iffully flooded with unborated water. The proposed TS change will revise TS Sections 3.7.16 and4.3 by eliminating restrictions on placement of low enriched uranium fuel assemblies in either the Unit 1 or Unit 2 SFP based on the use of partial soluble boron credit for soluble boron in the SFPs. This is accomplished by taking credit for soluble boron in accordance with 10 CFR 50.68. The current TSs are nonconservative with respect to spent fuel storage criteria. The licensee has implemented compensatory measures and the proposed amendments correct the nonconservative TSs. The licensee has determined that for normal conditions both of the boron-credited subcriticalityanalysis criteria in 10 CFR 50.68(b)(4) can be achieved if credit is taken for 200 ppm soluble boron in the SFPs. The current minimum boron concentration for the Catawba 1 and 2 SFPs as controlled through the Core Operating Limit Report (COLR) per TS 3.7.15 is 2700 ppm.
Catawba 1 and 2 currently complies with a design basis that requires preventing criticality in a spent fuel pool based on the K eff of the SFP storage racks loaded with fuel of the maximum fuelassembly reactivity not exceeding 0.95, at 95-percent probability, 95-percent confidence level, iffully flooded with unborated water. The proposed TS change will revise TS Sections 3.7.16 and4.3 by eliminating restrictions on placement of low enriched uranium fuel assemblies in either the Unit 1 or Unit 2 SFP based on the use of partial soluble boron credit for soluble boron in the SFPs. This is accomplished by taking credit for soluble boron in accordance with 10 CFR 50.68. The current TSs are nonconservative with respect to spent fuel storage criteria. The licensee has implemented compensatory measures and the proposed amendments correct the nonconservative TSs. The licensee has determined that for normal conditions both of the boron-credited subcriticalityanalysis criteria in 10 CFR 50.68(b)(4) can be achieved if credit is taken for 200 ppm soluble boron in the SFPs. The current minimum boron concentration for the Catawba 1 and 2 SFPs as controlled through the Core Operating Limit Report (COLR) per TS 3.7.15 is 2700 ppm.
Since the amendment request by the licensee now credits soluble boron, the licensee has completed a boron dilution analysis to demonstrate that potential boron dilution events will notresult in an SFP boron concentration below the acceptable minimum boron concentration of 200 ppm credited in the criticality analyses performed for the SFPs. The NRC staff's review ofthe licensee's boron dilution analysis is provided below.3.1 Boron Dilution Analysis The licensee performed a detailed boron dilution analysis in which the various boron dilutionscenarios for the Catawba 1 and 2 spent fuel pool were examined to ensure that sufficient time is available to detect and mitigate the dilution prior to the boron concentration falling below theminimum concentration required to maintain K eff below 0.95. The dilution events consideredincluded pipe breaks, misalignment of systems interfacing with spent fuel pool cooling, and safe shutdown facility (SSF) events in which the SFP is used as a source of cooling water and unborated make-up water is used to refill the pool. The potential dilution sources consideredincluded pipe breaks and system misalignments involving the following tan ks and systems:Fire ProtectionRecycle Hold-up Tanks (RHTs)
Since the amendment request by the licensee now credits soluble boron, the licensee has completed a boron dilution analysis to demonstrate that potential boron dilution events will notresult in an SFP boron concentration below the acceptable minimum boron concentration of 200 ppm credited in the criticality analyses performed for the SFPs. The NRC staff's review ofthe licensee's boron dilution analysis is provided below.3.1 Boron Dilution Analysis The licensee performed a detailed boron dilution analysis in which the various boron dilutionscenarios for the Catawba 1 and 2 spent fuel pool were examined to ensure that sufficient time is available to detect and mitigate the dilution prior to the boron concentration falling below theminimum concentration required to maintain K eff below 0.95. The dilution events consideredincluded pipe breaks, misalignment of systems interfacing with spent fuel pool cooling, and safe shutdown facility (SSF) events in which the SFP is used as a source of cooling water and unborated make-up water is used to refill the pool. The potential dilution sources consideredincluded pipe breaks and system misalignments involving the following tan ks and systems:Fire ProtectionRecycle Hold-up Tanks (RHTs)
Recycle MonitorTanks  Reactor Make-up Water Storage Tanks (RMWSTs)Low-Pressure Service Water Nuclear Service Water Standby Shutdown Facility Standby Make-up PumpEquipment Decontamination Drinking Water Make-up Demineralized Water Heated Water Reactor Building Ventilation Cooling WaterBased on its review of the various potential dilution events, the licensee concluded that theworst-case dilution scenario is one initiated by a "continuous flow" event involving the break of a 4-inch pipe in the non-seismic fire protecti on system. The postulated break may be one due toseismic or tornado activity, and is based on a break size of approximately 1.5 in 2, which resultsin a maximum flow rate of 701 gpm of unborated water to the SFP. TS LCO (limiting condition for operation) 3.7.15 states "The spent fuel pool boron concentrationshall be within the limit specified in the COLR."  In its boron dilution analysis the licensee assumed an initial SFP boron concentration of 2700 parts per million (ppm), which is theminimum boron concentration specified in the COLR. Based on the 2700 ppm initial pool boron concentration, a minimum starting pool volume of 374,403, gallons and an inflow of 701 gpm from the break of the fire protection line, the time required to dilute the pool to a boron concentration of 200 ppm, which corresponds to the K eff 0.95 safety limit was calculated to be32.36 hours, and the total volume of water required for the dilution was over 1.3 million gallons.Since for the worst case dilution event it would take over 32 hours to dilute a SFP to theconcentration required to maintain K eff below 0.95 (200 ppm), and would involve substantialoverflow of a SFP, the licensee will have ample time to detect, identify, and mitigate the dilutionevent. Operators will receive numerous indicators to alert them long before 32 hours haveelapsed. Among the indicators would be SFP level Hi/Lo alarms, flooding in the auxiliarybuilding, and observations via shift rounds. The alarm response procedures direct operations to restore the SFP level to normal, and contain guidance for make-up to the SFP, and instructions for barriers to preclude adding sufficient unborated water to dilute boron concentration below the COLR minimum allowed concentration, and guidance on syst emalignment for adding boric acid to the SFP, should it be needed. Low-flow, long-term dilution events in which the rate of inleakage of unborated waterapproximately matches normal water loss can also result in dilution of the SFP boron concentration. However, because of the large quantity of water required to dilute the SFP boron concentration to the 200 ppm minimum, the leak would have to go undetected for several weeks. The plant TS, SR 3.7.15.1, requires that every 7 days the spent fuel pool boronconcentration be verified to be within the limits specified in the COLR. Therefore, low-flow long-term dilution events will be detected as a result of the plants' normal surveillance, asrequired by the plants' TSs.The licensee analyzed the boron dilution event involving system misalignment and determinedthe worst-case dilution from a finite-source system misalignment involved aligning the SFP cooling to take suction on the RMWST, and allowing the RHTs to piggyback on the RMWST.
Recycle MonitorTanks  Reactor Make-up Water Storage Tanks (RMWSTs)Low-Pressure Service Water Nuclear Service Water Standby Shutdown Facility Standby Make-up PumpEquipment Decontamination Drinking Water Make-up Demineralized Water Heated Water Reactor Building Ventilation Cooling WaterBased on its review of the various potential dilution events, the licensee concluded that theworst-case dilution scenario is one initiated by a "continuous flow" event involving the break of a 4-inch pipe in the non-seismic fire protecti on system. The postulated break may be one due toseismic or tornado activity, and is based on a break size of approximately 1.5 in 2, which resultsin a maximum flow rate of 701 gpm of unborated water to the SFP. TS LCO (limiting condition for operation) 3.7.15 states "The spent fuel pool boron concentrationshall be within the limit specified in the COLR."  In its boron dilution analysis the licensee assumed an initial SFP boron concentration of 2700 parts per million (ppm), which is theminimum boron concentration specified in the COLR. Based on the 2700 ppm initial pool boron concentration, a minimum starting pool volume of 374,403, gallons and an inflow of 701 gpm from the break of the fire protection line, the time required to dilute the pool to a boron concentration of 200 ppm, which corresponds to the K eff 0.95 safety limit was calculated to be32.[[estimated NRC review hours::36 hours]], and the total volume of water required for the dilution was over 1.3 million gallons.Since for the worst case dilution event it would take over [[estimated NRC review hours::32 hours]] to dilute a SFP to theconcentration required to maintain K eff below 0.95 (200 ppm), and would involve substantialoverflow of a SFP, the licensee will have ample time to detect, identify, and mitigate the dilutionevent. Operators will receive numerous indicators to alert them long before [[estimated NRC review hours::32 hours]] haveelapsed. Among the indicators would be SFP level Hi/Lo alarms, flooding in the auxiliarybuilding, and observations via shift rounds. The alarm response procedures direct operations to restore the SFP level to normal, and contain guidance for make-up to the SFP, and instructions for barriers to preclude adding sufficient unborated water to dilute boron concentration below the COLR minimum allowed concentration, and guidance on syst emalignment for adding boric acid to the SFP, should it be needed. Low-flow, long-term dilution events in which the rate of inleakage of unborated waterapproximately matches normal water loss can also result in dilution of the SFP boron concentration. However, because of the large quantity of water required to dilute the SFP boron concentration to the 200 ppm minimum, the leak would have to go undetected for several weeks. The plant TS, SR 3.7.15.1, requires that every 7 days the spent fuel pool boronconcentration be verified to be within the limits specified in the COLR. Therefore, low-flow long-term dilution events will be detected as a result of the plants' normal surveillance, asrequired by the plants' TSs.The licensee analyzed the boron dilution event involving system misalignment and determinedthe worst-case dilution from a finite-source system misalignment involved aligning the SFP cooling to take suction on the RMWST, and allowing the RHTs to piggyback on the RMWST.
The result of this misalignment event would be an introduction of just over 226,000 gallons of  unborated water to a SFP, which is not a sufficient amount to dilute the pool boronconcentration below the 200 ppm safety limit. The licensee also determined that the worst-case dilution from an infinite-source misalignment results from aligning SFP cooling to take suction from nuclear service water. At a nominal rate of 140 gpm, the 200 ppm boron safety limit would be reached in just under 83 hours. Therefore this dilution case is bounded by the fire protection pipe break.The only credible scenario during a standby shutdown facility (SSF) event is for the SSFstandby make-up pump to take suction on a SFP for up to 72 hours for reactor coolant pump seal injection. After 72 hours the pump is secured, and the SFP make-up could occur using unborated water. The licensee determined that in the worst-case scenario the final concentration of the SFP water will be 1324 ppm boron which is well above the safety limit of200 ppm boron concentration. The licensee also indicated that since the SFP cooli ng syst emoperates at a higher pressure than the component cooli ng system, any dilution via SFP coolingheat exchanger leakage is not expected. The licensee has analyzed various potential dilution events and has concluded that unplannedand inadvertent events would not result in the dilution of a SFP to boron concentration less thanthat required to maintain K eff below 0.95. The NRC staff has reviewed the results of thelicensees boron dilution evaluations. The minimum concentration of boron required for the K effin a SFP remains below 0.95 and is assured based on the following*The flow rates associated with the dilution events
The result of this misalignment event would be an introduction of just over 226,000 gallons of  unborated water to a SFP, which is not a sufficient amount to dilute the pool boronconcentration below the 200 ppm safety limit. The licensee also determined that the worst-case dilution from an infinite-source misalignment results from aligning SFP cooling to take suction from nuclear service water. At a nominal rate of 140 gpm, the 200 ppm boron safety limit would be reached in just under [[estimated NRC review hours::83 hours]]. Therefore this dilution case is bounded by the fire protection pipe break.The only credible scenario during a standby shutdown facility (SSF) event is for the SSFstandby make-up pump to take suction on a SFP for up to [[estimated NRC review hours::72 hours]] for reactor coolant pump seal injection. After [[estimated NRC review hours::72 hours]] the pump is secured, and the SFP make-up could occur using unborated water. The licensee determined that in the worst-case scenario the final concentration of the SFP water will be 1324 ppm boron which is well above the safety limit of200 ppm boron concentration. The licensee also indicated that since the SFP cooli ng syst emoperates at a higher pressure than the component cooli ng system, any dilution via SFP coolingheat exchanger leakage is not expected. The licensee has analyzed various potential dilution events and has concluded that unplannedand inadvertent events would not result in the dilution of a SFP to boron concentration less thanthat required to maintain K eff below 0.95. The NRC staff has reviewed the results of thelicensees boron dilution evaluations. The minimum concentration of boron required for the K effin a SFP remains below 0.95 and is assured based on the following*The flow rates associated with the dilution events
*The large volume of water required for dilution
*The large volume of water required for dilution
*The long dilution times associated with the events
*The long dilution times associated with the events
*The SFP level detection alarms coupled with operator surveillance *Plant procedures to control SFP water level 3.2Criticality Analysis
*The SFP level detection alarms coupled with operator surveillance *Plant procedures to control SFP water level 3.2Criticality Analysis 3.2.1 Criticality Analysis Codes The code employed in the licensee's SFP criticality analysis is SCALE 4.4/KENO V.a. KENOV.a is a 3-D Monte Carlo criticality module in the SCALE 4.4 package. The licensee has performed a SCALE 4.4/KENO V.a benchmark analysis to determine calculational biases and uncertainties. The criticality analysis for the Catawba 1 and 2 new fuel storage vaults (NFVs) and SFPs hasbeen performed in accordance with the requirements of 10 CFR 50.68(b). This evaluation takes partial credit for soluble boron in the SFPs. The analysis determined that the Catawba 1 and 2 NFVs and SFPs can store unirradiated fuel up to 5 wt % U-235, with no location restrictions.The maximum 95/95 K eff for the NFV analysis was calculated to be 0.9324, meeting therequirements of 10 CFR 50.68(b)(2) and (3). For the Catawba 1 and 2 SFP criticality analyses, the maximum 95/95 K eff with no boron in theSFP was calculated to be 0.9680. This meets the no-boron 95/95 K eff < 1.0 criterion in10 CFR 50.68(b)(4). The SFP evaluation also confirmed that with 200 ppm of partial solubleboron credit, the maximum 95/95 K eff of 0.9294 remains well below the regulatory requirementthat the maximum 95/95 K eff be less than 0.95 for all normal conditions. The current minimum boron concentration required in the Catawba 1 and 2 SFPs (2700 ppm) isadequate to maintain the maximum 95/95 K eff below 0.95 for all credible accident scenarios inthe Catawba 1 and 2 SFPs.3.2.2 Bias and Uncertainty The NRC SFP criticality analysis guidance specifies that the maximum K eff value for thecriticality analysis should be the summation of the calculated nominal K eff, the bias in criticalityanalysis methods, manufacturing and calculational uncertainties, and the correction for the effect of the axial distribution in burnup when credit for burnup is taken. Uncertainties should be determined for the proposed storage facilities and fuel assemblies to account for tolerances inthe mechanical and material specifications. An acceptable method for determining the maximum reactivity may be either (1) a worst-case combination with mechanical and material conditions set to maximize K eff, or (2) a sensitivity study of the reactivity effects of tolerancevariations. If used, a sensitivity study should indicate all possible significant variations (tolerances) in the material and mechanical specifications of the racks; the results may bestatistically combined provided they are independent variations. Combinations of the two methods may also be used.The licensee has performed a SCALE 4.4/KENO V.a benchmark analysis of critical experimentsto determine calculational biases and uncertainties for both the 44-group and 238-group cross-section libraries included with the SCALE 4.4 package. For Catawba 1 and 2 criticality applications, the SCALE 4.4/KENO V.a method biases anduncertainties are based on analysis of 41 LEU critical experiments performed by Pacific Northwest Laboratories. These critical experiments model various square-pitch arrangements of fuel rods, and include both over- and under-moderated lattices. Because the NFV and SFP analyses model fresh fuel at only the highest permissible enrichment(5.00 +/- 0.05 wt % U-235), each of the 41 critical experiments selected was at the highestenrichment available (4.31 wt % U-235). The results from the benchmark analyses indicated that the 238-group cross-section libraryyields the more consistent results (i.e., smaller variations in reactivity bias) across the range of moderation in the selected critical experiments. Therefore, the 238-group cross-section library is used for all the SCALE 4.4/KENO V.a computations performed in the Catawba 1 and 2 NFV andSFPs criticality analyses. SCALE 4.4/KENO V.a modeling of these 41 critical experiments with the 238-group libraryyielded a benchmark calculational bias of +0.0061 k (average under-prediction of K eff) and anuncertainty of +/-0.0071 k. This bias and uncertainty are used in determining the total bounding 95/95 system K effs for each NFV or SFPs storage configuration. They were analyzed with  SCALE 4.4/KENO V.a. and provide the results of the Catawba 1 and 2 NFV and SFPs criticalityevaluations, respectively.3.2.3 Computation of the Maximum 95/95 K effFor every fuel assembly design that is considered in the scope of the Catawba 1 and 2 SFPsand NFV criticality analyses, a nominal K eff is calculated. This K eff is only the base value,however. A total K eff is determined by adding several pertinent reactivity biases anduncertainties, to provide an overall 95-percent probability, at a 95-percent confidence level(95/95), that the true system K eff does not exceed the 95/95 K eff for that particular storagecondition. Table 4 in the licensee's September 13, 2005, application lists the various biases anduncertainties that are considered in the Catawba 1 and 2 NFV and SFPs criticality analyses.
 
====3.2.1 Criticality====
Analysis Codes The code employed in the licensee's SFP criticality analysis is SCALE 4.4/KENO V.a. KENOV.a is a 3-D Monte Carlo criticality module in the SCALE 4.4 package. The licensee has performed a SCALE 4.4/KENO V.a benchmark analysis to determine calculational biases and uncertainties. The criticality analysis for the Catawba 1 and 2 new fuel storage vaults (NFVs) and SFPs hasbeen performed in accordance with the requirements of 10 CFR 50.68(b). This evaluation takes partial credit for soluble boron in the SFPs. The analysis determined that the Catawba 1 and 2 NFVs and SFPs can store unirradiated fuel up to 5 wt % U-235, with no location restrictions.The maximum 95/95 K eff for the NFV analysis was calculated to be 0.9324, meeting therequirements of 10 CFR 50.68(b)(2) and (3). For the Catawba 1 and 2 SFP criticality analyses, the maximum 95/95 K eff with no boron in theSFP was calculated to be 0.9680. This meets the no-boron 95/95 K eff < 1.0 criterion in10 CFR 50.68(b)(4). The SFP evaluation also confirmed that with 200 ppm of partial solubleboron credit, the maximum 95/95 K eff of 0.9294 remains well below the regulatory requirementthat the maximum 95/95 K eff be less than 0.95 for all normal conditions. The current minimum boron concentration required in the Catawba 1 and 2 SFPs (2700 ppm) isadequate to maintain the maximum 95/95 K eff below 0.95 for all credible accident scenarios inthe Catawba 1 and 2 SFPs.3.2.2 Bias and Uncertainty The NRC SFP criticality analysis guidance specifies that the maximum K eff value for thecriticality analysis should be the summation of the calculated nominal K eff, the bias in criticalityanalysis methods, manufacturing and calculational uncertainties, and the correction for the effect of the axial distribution in burnup when credit for burnup is taken. Uncertainties should be determined for the proposed storage facilities and fuel assemblies to account for tolerances inthe mechanical and material specifications. An acceptable method for determining the maximum reactivity may be either (1) a worst-case combination with mechanical and material conditions set to maximize K eff, or (2) a sensitivity study of the reactivity effects of tolerancevariations. If used, a sensitivity study should indicate all possible significant variations (tolerances) in the material and mechanical specifications of the racks; the results may bestatistically combined provided they are independent variations. Combinations of the two methods may also be used.The licensee has performed a SCALE 4.4/KENO V.a benchmark analysis of critical experimentsto determine calculational biases and uncertainties for both the 44-group and 238-group cross-section libraries included with the SCALE 4.4 package. For Catawba 1 and 2 criticality applications, the SCALE 4.4/KENO V.a method biases anduncertainties are based on analysis of 41 LEU critical experiments performed by Pacific Northwest Laboratories. These critical experiments model various square-pitch arrangements of fuel rods, and include both over- and under-moderated lattices. Because the NFV and SFP analyses model fresh fuel at only the highest permissible enrichment(5.00 +/- 0.05 wt % U-235), each of the 41 critical experiments selected was at the highestenrichment available (4.31 wt % U-235). The results from the benchmark analyses indicated that the 238-group cross-section libraryyields the more consistent results (i.e., smaller variations in reactivity bias) across the range of moderation in the selected critical experiments. Therefore, the 238-group cross-section library is used for all the SCALE 4.4/KENO V.a computations performed in the Catawba 1 and 2 NFV andSFPs criticality analyses. SCALE 4.4/KENO V.a modeling of these 41 critical experiments with the 238-group libraryyielded a benchmark calculational bias of +0.0061 k (average under-prediction of K eff) and anuncertainty of +/-0.0071 k. This bias and uncertainty are used in determining the total bounding 95/95 system K effs for each NFV or SFPs storage configuration. They were analyzed with  SCALE 4.4/KENO V.a. and provide the results of the Catawba 1 and 2 NFV and SFPs criticalityevaluations, respectively.3.2.3 Computation of the Maximum 95/95 K effFor every fuel assembly design that is considered in the scope of the Catawba 1 and 2 SFPsand NFV criticality analyses, a nominal K eff is calculated. This K eff is only the base value,however. A total K eff is determined by adding several pertinent reactivity biases anduncertainties, to provide an overall 95-percent probability, at a 95-percent confidence level(95/95), that the true system K eff does not exceed the 95/95 K eff for that particular storagecondition. Table 4 in the licensee's September 13, 2005, application lists the various biases anduncertainties that are considered in the Catawba 1 and 2 NFV and SFPs criticality analyses.
Each of these biases and uncertainties is discussed in more detail below:
Each of these biases and uncertainties is discussed in more detail below:
*Benchmark Method BiasThis bias is determined from the benchmarking of the c ode system used (SCALE4.4/KENO V.a), and represents how much the code system is expected to over predict(negative bias) or under predict (positive bias) the "true K eff" of the physical system beingmodeled. The bias for SCALE 4.4/KENO V.a with its 238- group cross-section library is
*Benchmark Method BiasThis bias is determined from the benchmarking of the c ode system used (SCALE4.4/KENO V.a), and represents how much the code system is expected to over predict(negative bias) or under predict (positive bias) the "true K eff" of the physical system beingmodeled. The bias for SCALE 4.4/KENO V.a with its 238- group cross-section library is

Revision as of 13:12, 13 July 2019

License Amendments 233 and 229 Revised Storage Criteria for Low-enriched Uranium Fuel
ML062540237
Person / Time
Site: Catawba  Duke Energy icon.png
Issue date: 09/27/2006
From: Stang J
NRC/NRR/ADRO/DORL/LPLII-1
To: Jamil D
Duke Power Co
Stang J, NRR/DORL, 415-1345
References
TAC MC8439, TAC MC8440
Download: ML062540237 (25)


Text

September 27, 2006Mr. Dhiaa JamilVice President Catawba Nuclear Station Duke Power Company LLC 4800 Concord Road York, SC 29745

SUBJECT:

CATAWBA NUCLEAR STATION, UNITS 1 AND 2, ISSUANCE OFAMENDMENTS REGARDING REVISED STORAGE CRITERIA FOR LOW-ENRICHED URANIUM FUEL (TAC NOS. MC8439 and MC8440)

Dear Mr. Jamil:

The Nuclear Regulatory Commission has issued the enclosed Amendment No. 233 toRenewed Facility Operating License NPF-35 and Amendment No. 229 to Renewed FacilityOperating License NPF-52 for the Catawba Nuclear Station, Units 1 and 2, respectively. Theamendments consist of changes to the Technical Specifications (TSs) in response to your application dated September 13, 2005, as supplemented March 20, 2006. The amendments revise a nonconservative TS associated with spent fuel storage in the spentfuel pool. The licensee identified the nonconservative TS while comparing results from spent fuel pool criticality codes.A copy of the related Safety Evaluation is also enclosed. A Notice of Issuance will be incl udedin the Commission's biweekly Federal Register notice. Sincerely,/RA/John Stang, Senior Project ManagerPlant Licensing Branch II-1 Division of Operating Reactor Licensing Office of Nuclear Reactor RegulationDocket Nos. 50-413 and 50-414

Enclosures:

1. Amendment No. 233 to NPF-35
2. Amendment No. 229 to NPF-52
3. Safety Evaluationcc w/encls: See next page September 27, 2006Mr. Dhiaa Jamil Vice President Catawba Nuclear Station Duke Power Company LLC 4800 Concord Road York, SC 29745

SUBJECT:

CATAWBA NUCLEAR STATION, UNITS 1 AND 2, ISSUANCE OFAMENDMENTS REGARDING REVISED STORAGE CRITERIA FOR LOW-ENRICHED URANIUM FUEL (TAC NOS. MC8439 and MC8440)

Dear Mr. Jamil:

The Nuclear Regulatory Commission has issued the enclosed Amendment No. 233 toRenewed Facility Operating License NPF-35 and Amendment No. 229 to Renewed FacilityOperating License NPF-52 for the Catawba Nuclear Station, Units 1 and 2, respectively. Theamendments consist of changes to the Technical Specifications (TSs) in response to your application dated September 13, 2005, as supplemented March 20, 2006. The amendments revise a nonconservative TS associated with spent fuel storage in the spentfuel pool. The licensee identified the nonconservative TS while comparing results from spent fuel pool criticality codes.A copy of the related Safety Evaluation is also enclosed. A Notice of Issuance will be incl udedin the Commission's biweekly Federal Register notice. Sincerely,/RA/John Stang, Senior Project Manager Plant Licensing Branch II-1 Division of Operating Reactor Licensing Office of Nuclear Reactor RegulationDocket Nos. 50-413 and 50-414

Enclosures:

1. Amendment No. 233 to NPF-35
2. Amendment No. 229 to NPF-52
3. Safety Evaluationcc w/encls: See next page DISTRIBUTION: PublicRidsAcrsAcnwMailCenter RidsNrrSbpc (CLi)LPL2-1 R/FGHill(4 hard copies)FForsaty, NRR RidsNrrDorlLpl2-1(EMarinos)RidsNrrDirsItsb(TKobetz)

RidsNrrPMJStang(hard copy)RidsRgn2MailCenter(MErnstes)RidsNrrLAMO'Brien(hard copy)RidsNrrDorlDpr RidsOgcRpRidsNrrSbpb (AStubbs)Package No. ML062710490 Amendment No. ML062540237Tech Spec No. ML062710596*SE input date NRR-058OFFICENRR/LPL2-1/PMNRR/LPL2-1/LANRR/SBPB/ABCOGCNRR/LPL2-1/BCNAMEJStang :klrMO'BrienCLi*JMartin (nlo w/comments)EMarinosDATE09/12/0609/12/0606/21/0609/26/0609/27/06OFFICIAL RECORD COPY Catawba Nuclear Station, Units 1 & 2 Page 1 of 2 cc:

Mr. Randy Hart, ManagerRegulatory Compliance Duke Energy Corporation 4800 Concord Road York, South Carolina 29745Ms. Lisa F. VaughnDuke Energy Corporation 526 South Church Street P. O. Box 1006 Mail Code = EC07H Charlotte, North Carolina 28201-1006North Carolina Municipal Power Agency Number 1 1427 Meadowwood Boulevard P.O. Box 29513 Raleigh, North Carolina 27626County Manager of York CountyYork County Courthouse York, South Carolina 29745Piedmont Municipal Power Agency 121 Village DriveGreer, South Carolina 29651Ms. Karen E. LongAssistant Attorney General North Carolina Department of Justice

P.O. Box 629 Raleigh, North Carolina 27602NCEM REP Program Manager4713 Mail Service Center Raleigh, North Carolina 27699-4713North Carolina Electric Membership Corp.P.O. Box 27306 Raleigh, North Carolina 27611Senior Resident InspectorU.S. Nuclear Regulatory Commission 4830 Concord Road York, South Carolina 29745Mr. Henry Porter, Assistant DirectorDivision of Waste Management Bureau of Land and Waste Management Dept. of Health and Environmental Control 2600 Bull Street Columbia, South Carolina 29201-1708Mr. R.L. Gill, Jr., Manager Nuclear Regulatory Issues and Industry Affairs Duke Energy Corporation 526 South Church Street Mail Stop EC05P Charlotte, North Carolina 28202Saluda River Electric P.O. Box 929 Laurens, South Carolina 29360Mr. Peter R. Harden, IV, Vice PresidentCustomer Relations and Sales Westinghouse Electric Company 6000 Fairview Road 12th Floor Charlotte, North Carolina 28210Mr. T. Richard PuryearOwners Group (NCEMC)

Duke Energy Corporation 4800 Concord Road York, South Carolina 29745 Catawba Nuclear Station, Units 1 & 2 cc:

Division of Radiation ProtectionNC Dept. of Environment, Health, and Natural Resources 3825 Barrett Drive Raleigh, North Carolina 27609-7721Mr. Henry BarronGroup Vice President, Nuclear Generation and Chief Nuclear Officer P.O. Box 1006-EC07H Charlotte, NC 28201-1006Page 2 of 2 DUKE POWER COMPANY LLCNORTH CAROLINA ELECTRIC MEMBERSHIP CORPORATIONSALUDA RIVER ELECTRIC COOPERATIVE, INC.DOCKET NO. 50-413CATAWBA NUCLEAR STATION, UNIT 1AMENDMENT TO RENEWED FACILITY OPERATING LICENSEAmendment No. 233Renewed License No. NPF-351.The Nuclear Regulatory Commission (the Commission) has found that:A.The application for amendment to the Catawba Nuclear Station, Unit 1 (the facility)Renewed Facility Operating License No. NPF-35 filed by the Duke Power Com panyLLC, acting for itself, North Carolina Electric Membership Corporation and Saluda River Electric Cooperative, Inc. (licensees), dated September 13, 2005, as supplemented March 20, 2006, complies with the standards and requirements of the Atomic Energy Act of 1954, as amended (the Act), and the Commission's rules and regulations as set forth in 10 CFR Chapter I;B.The facility will operate in conformity with the application, the provisions of the Act,and the rules and regulations of the Commission;C.There is reasonable assurance (I) that the activities authorized by this amendmentcan be conducted without endangering the health and safety of the public, and (ii) that such activities will be conducted in compliance with the Commission'sregulations set forth in 10 CFR Chapter I;D.The issuance of this amendment will not be inimical to the common defense andsecurity or to the health and safety of the public; and E.The issuance of this amendment is in accordance with 10 CFR Part 51 of theCommission's regulations and all applicable requirements have been satisfied. 2.Accordingly, the license is hereby amended by page changes to the TechnicalSpecifications as indicated in the attachment to this license amendment, and paragraph 2.C.(2) of Renewed Facility Operating License No. NPF-35 is hereby amended to readas follows:(2)Technical SpecificationsThe Technical Specifications contained in Appendix A, as revised throughAmendment No. 233, which are attached hereto, are hereby incorporated into this license. Duke Power Company LLC shall operate the facility inaccordance with the Technical Specifications. 3.This license amendment is effective as of its date of issuance and shall be implementedwithin 60 days of issuance. FOR THE NUCLEAR REGULATORY COMMISSION/RA/Evangelos C. Marinos, ChiefPlant Licensing Branch II-1 Division of Operating Reactor Licensing Office of Nuclear Reactor Regulation

Attachment:

Changes to License No. NPF-35 and the Technical SpecificationsDate of Issuance: September 27, 2006 DUKE POWER COMPANY LLCNORTH CAROLINA MUNICIPAL POWER AGENCY NO. 1PIEDMONT MUNICIPAL POWER AGENCYDOCKET NO. 50-414CATAWBA NUCLEAR STATION, UNIT 2AMENDMENT TO RENEWED FACILITY OPERATING LICENSEAmendment No. 229Renewed License No. NPF-521.The Nuclear Regulatory Commission (the Commission) has found that:A.The application for amendment to the Catawba Nuclear Station, Unit 2 (the facility)Renewed Facility Operating License No. NPF-52 filed by the Duke Power Com panyLLC, acting for itself, North Carolina Municipal Power Agency No. 1 and Piedmont Municipal Power Agency (licensees), dated September 13, 2005, as supplemented March 20, 2006, complies with the standards and requirements of the AtomicEnergy Act of 1954, as amended (the Act), and the Commission's rules and regulations as set forth in 10 CFR Chapter I;B.The facility will operate in conformity with the application, the provisions of the Act,and the rules and regulations of the Commission;C.There is reasonable assurance (I) that the activities authorized by this amendmentcan be conducted without endangering the health and safety of the public, and (ii) that such activities will be conducted in compliance with the Commission'sregulations set forth in 10 CFR Chapter I;D.The issuance of this amendment will not be inimical to the common defense andsecurity or to the health and safety of the public; and E.The issuance of this amendment is in accordance with 10 CFR Part 51 of theCommission's regulations and all applicable requirements have been satisfied. 2.Accordingly, the license is hereby amended by page changes to the TechnicalSpecifications as indicated in the attachment to this license amendment, and Paragraph 2.C.(2) of Renewed Facility Operating License No. NPF-52 is hereby amended to readas follows:(2)Technical SpecificationsThe Technical Specifications contained in Appendix A, as revised throughAmendment No. 229 , which are attached hereto, are hereby incorporated into this license. Duke Power Company LLC shall operate the facility inaccordance with the Technical Specifications.3.This license amendment is effective as of its date of issuance and shall be implementedwithin 60 days of issuance. FOR THE NUCLEAR REGULATORY COMMISSION/RA/Evangelos C. Marinos, Chief Plant Licensing Branch II-1 Division of Operating Reactor Licensing Office of Nuclear Reactor Regulation

Attachment:

Changes to License No. NPF-52 and the Technical Specifications Date of Issuance: September 27, 2006 ATTACHMENT TO LICENSE AMENDMENT NO. 233 RENEWED FACILITY OPERATING LICENSE NO. NPF-35 DOCKET NO. 50-413AND LICENSE AMENDMENT NO. 229RENEWED FACILITY OPERATING LICENSE NO. NPF-52DOCKET NO. 50-414Replace the following pages of the Renewed Facility Operating Licenses and Appendix ATechnical Specifications (TSs) with the attached revised pages. The revised pages are identified by amendment number and contain marginal lines indicating the areas of change. RemoveInsertLicensesLicensesLicense No. NPF-35, page 4License No. NPF-35, page 4License No. NPF-52, page 4License No. NPF-52, page 4TSsTSs3.7.16-13.7.16-13.7.16-23.7.16-2 3.7.16-33.7.16-3 4.0-24.0-2 B 3.7.15-1B 3.7.15-1 B 3.7.15-2B 3.7.15-2 B 3.7.15-3B 3.7.15-3B 3.7.15-4B 3.7.16-1B 3.7.16-1 B 3.7.16-2B 3.7.16-2 B 3.7.16-3B 3.7.16-3B 3.7.16-4 SAFETY EVALUATION BY THE OFFICE OF NUCLEAR REACTOR REGULATIONRELATED TOAMENDMENT NO. 233 TO RENEWED FACILITY OPERATING LICENSE NPF-35ANDAMENDMENT NO. 229 TO RENEWED FACILITY OPERATING LICENSE NPF-52DUKE POWER COMPANY LLCCATAWBA NUCLEAR STATION, UNITS 1 AND 2DOCKET NOS. 50-413 AND 50-41

41.0 INTRODUCTION

By application dated September 13, 2005 (Agencywide Documents Access and ManagementSystem (ADAMS) Accession No. ML052590247), as supplemented by letter dated March 20, 2006 (ADAMS Accession No. ML060880447), Duke Power Company LLC (Duke, the licensee),

requested changes to the Technical Specifications (TSs) for the Catawba Nuclear Station,Units 1 and 2 (Catawba 1 and 2). The supplement dated March 20, 2006, provided additional information that clarified the application, did not expand the scope of the application asoriginally noticed, and did not change the Nuclear Regulatory Commission (NRC) staff's originalproposed no significant hazards consideration determination as published the Federal Registeron November 21, 2005 (70 FR 70104).The proposed changes would revise TSs Section 3.7.16, "Spent Fuel Assembly Storage," andSection 4.3, "Fuel Storage." The amendment revises the storage criteria for low-enricheduranium fuel stored at Catawba 1 and 2 to correct the nonconservative TSs. This is accomplished by taking partial credit for soluble boron in the Catawba 1 and 2 spent fuel pool, in accordance with the regulatory requirements of Title 10 of the Code of Federal Regulations(10 CFR), Part 50, Section 50.68(b).

2.0 REGULATORY EVALUATION

Appendix A of, 10 CFR Part 50, General Design Criterion (GDC) 62, "Prevention of criticality infuel storage and handling," states, "Criticality in the fuel storage and handling system shall beprevented by physical systems or processes, preferably by use of geometrically safeconfigurations." In NUREG-0800 "Standard Review Plan," Section 9.1.2, the NRC hasestablished a five-percent subcriticality margin (K-effective 0.95) for nuclear power plant operators to comply with GDC 62. Section 50.68, "Criticality accident requirements," states in subpart 50.68(b)(4), "If credit istaken for soluble boron, the k-effective of the spent fuel storage racks loaded with fuel of themaximum fuel assembly reactivity must not exceed 0.95, at a 95 percent probability, 95 percentconfidence level, if flooded with borated water, and the k-effective must remain below 1.0 (subcritical), at a 95 percent confidence level, if flooded with unborated water."The NRC staff, has accepted Westinghouse Owners Group Topical Report WCAP-14416-P inlicensing applications to credit soluble boron in spent fuel pool criticality. The review and acceptance of WCAP-14416-P focused on the methodology whereby credit could be taken for soluble boron in the spent fuel pool (SFP) to meet the NRC-recommended criteria statedpreviously. All licensee's proposing to use this method for soluble boron credit are required to identify potential events which could dilute the SFP soluble boron to the concentration requiredto maintain the 0.95 k-effective limit in accordance with 10 CFR 50.68. They were also advised to quantify the time span of these dilution events to show that sufficient time is available to enable detection and mitigation of any dilution event. The SFPs storage and SFPs cooling systems are described in Chapter 9 of the Catawba1 and2 Updated Final Safety Analysis Report (UFSAR). The information provided by the licensee in its license amendment request dated September 13, 2005, and its response to the NRC staff'srequest for additional information, dated March 20, 2006, along with the applicable design-basis information in the Catawba 1 and 2 UFSAR, provide criteria needed to evaluate the ability ofequipment to comply with the appropriate requirements of 10 CFR 50.68 and NRC-approvedWCAP recommendations, as relates to proposed license amendment request changes. Several provisions of the NRC regulations and the licensees' plant operating licenses TSspertain to spent fuel pool criticality. The NRC regulations for preventing spent fuel poolcriticality include the general design criteria for nuclear power plants (10 CFR Part 50, Appendix A) and 10 CFR 50.68, while 10 CFR 70.24, "Criticality accident requirements,"

contains requirements for detection of an SFP criticality event.Appendix A to 10 CFR Part 50 and the plant safety analyses require or commit licensees todesign and test safety-related structures, systems, and components (SSCs) to provideadequate assurance that they can perform their safety functions. The NRC staff applies thesecriteria to plants with construction permits issued on or after May 21, 1971, and to plants whose licensees have committed to them. With respect to spent fuel pool criticality, the applicable General Design Criterion (GDC) is GDC 62, "Prevention of criticality in fuel storage and handling." GDC 62 states "Criticality in the fuel storage and handling system shall be preventedby physical systems or processes, preferably by the use of geometrically safe configurations." As written, GDC 62 emphasizes the prevention of an inadvertent criticality in the spent fuel poolas opposed to detection and mitigation. The preferred method of prevention is the use ofgeometrically safe configurations.Section 70.24(a) of 10 CFR 70.24 states that each licensee authorized to possess specialnuclear material in excess of certain defined quantities must maintain in each area in which such licensed special nuclear material is handled, used, or stored, a monitoring system capableof detecting a criticality that produces either (1) a defined absorbed dose or (2) a specific radiation level. The date of the facility's licensing determines whether the dose or radiation level requirements apply. In the mid-1990s the nuclear industry and NRC staff determi ned thata number of facilities had not maintained a criticality-monitoring system in accordance with the requirements of 10 CFR 70.24. Recognizing that numerous licensees were out of compliancewith 10 CFR 70.24 due to a regulatory oversight in the issuance of their operating licenses andrealizing that t he system required by 10 CFR 70.24 emphasized detection of a criticality eventrather than prevention, the staff issued Information Notice (IN) 97-77, "Exemption from the Requirements of Section 70.24 of Title 10 of the Code of Federal Regulations." IN 97-77 provided the staff's criteria for evaluating exemptions from 10 CFR 70.24. The staff's seven criteria, if satisfied, ensured that a licensee complied with GDC 62. The criteria emphasized prevention of spent fuel pool criticality rather than detection. Most licensees followed this approach and the staff issued a number of exemptions to 10 CFR 70.24 based on the criteria in IN 97-77.In 1998, the staff published 10 CFR 50.68 to formally issue the staff's criteria from IN 97-77with minor but notable changes, as regulatory requirements for ensuring subcriticality in spent fuel pools. Part 50 licensees may choose to comply with 10 CFR 50.68 in lieu of installing andmaintaining a criticality-monitoring system as required by 10 CFR 70.24 or seeking anexemption from 10 CFR 70.24. A licensee's compliance with 10 CFR 50.68 ensures that aninadvertent criticality in the spent fuel pool is extremely unlikely. Section 50.68 requires that licensees demonstrate that subcritical conditions (K eff < 1.0) can be maintained in the spent fuelpool under normal conditions without a soluble boron credit. However, under 10 CFR 50.68, licensees may credit soluble boron both during normal conditions to maintain a 5-percent subcriticality margin (K eff 0.95) and during accident conditions to maintain the spent fuel poolsubcritical (K eff < 1.0). Specifically, 10 CFR 50.68(b)(1) states "Plant procedures shall prohibitthe handling and storage at any one time of more fuel assemblies than have been determined to be safely subcritical under the most adverse moderation conditions feasible by unborated water." This requirement assures public health and safety during all fuel handling and storage operations, including cask loading, unloading, and handling, because subcritical conditions are maintained by geometrically safe configurations, in accordance with GDC 62. Therefore, the soluble boron in the spent fuel pool is available to ensure defense-in-depth requirements are satisfied under accident conditions.Since the issuance of 10 CFR 50.68 in 1998, numerous facilities have requested licenseamendment changes to take advantage of this new regulation. Many licensees have submitted license amendment requests (LARs) to rerack the spent fuel pool in accordance with the subcriticality requirements in 10 CFR 50.68. Under 10 CFR 50.68, licensees may credit soluble boron to demonstrate that the spent fuelpool storage racks can maintain a 5-percent subcriticality margin. By permitting a soluble boroncredit for normal storage conditions, 10 CFR 50.68 gives licensees more flexibility than wasavailable under 10 CFR 70.24 and 10 CFR 70.24 exemptions, where licensees were required to maintain the 5-percent subcriticality margin without a soluble boron credit. However, a licensee who takes advantage of the greater flexibility of 10 CFR 50.68 must also show that the s pentfuel pool will remain subcritical if flooded with unborated water. This second requirementensures that the full soluble boron concentration is available to prevent credible accidents fromresulting in an inadvertent criticality. The NRC defines acceptable methodologies for performing criticality analyses in the followingdocuments:1.NUREG-0800, Standard Review Plan, Section 9.1.2, Draft Revision 4, "Spent FuelStorage".2.NRC Memorandum from L. Kopp to T. Collins, "Guidance on the RegulatoryRequirements for Criticality Analysis of Fuel Storage at Light-Water Reactor Power Plants," August 19, 1998. The NRC staff used these documents to assist in its review ofthe licensee's LAR to ensure compliance with GDC 62 and 10 CFR 50.68.

3.0 TECHNICAL EVALUATION

Catawba 1 and 2 currently complies with a design basis that requires preventing criticality in a spent fuel pool based on the K eff of the SFP storage racks loaded with fuel of the maximum fuelassembly reactivity not exceeding 0.95, at 95-percent probability, 95-percent confidence level, iffully flooded with unborated water. The proposed TS change will revise TS Sections 3.7.16 and4.3 by eliminating restrictions on placement of low enriched uranium fuel assemblies in either the Unit 1 or Unit 2 SFP based on the use of partial soluble boron credit for soluble boron in the SFPs. This is accomplished by taking credit for soluble boron in accordance with 10 CFR 50.68. The current TSs are nonconservative with respect to spent fuel storage criteria. The licensee has implemented compensatory measures and the proposed amendments correct the nonconservative TSs. The licensee has determined that for normal conditions both of the boron-credited subcriticalityanalysis criteria in 10 CFR 50.68(b)(4) can be achieved if credit is taken for 200 ppm soluble boron in the SFPs. The current minimum boron concentration for the Catawba 1 and 2 SFPs as controlled through the Core Operating Limit Report (COLR) per TS 3.7.15 is 2700 ppm.

Since the amendment request by the licensee now credits soluble boron, the licensee has completed a boron dilution analysis to demonstrate that potential boron dilution events will notresult in an SFP boron concentration below the acceptable minimum boron concentration of 200 ppm credited in the criticality analyses performed for the SFPs. The NRC staff's review ofthe licensee's boron dilution analysis is provided below.3.1 Boron Dilution Analysis The licensee performed a detailed boron dilution analysis in which the various boron dilutionscenarios for the Catawba 1 and 2 spent fuel pool were examined to ensure that sufficient time is available to detect and mitigate the dilution prior to the boron concentration falling below theminimum concentration required to maintain K eff below 0.95. The dilution events consideredincluded pipe breaks, misalignment of systems interfacing with spent fuel pool cooling, and safe shutdown facility (SSF) events in which the SFP is used as a source of cooling water and unborated make-up water is used to refill the pool. The potential dilution sources consideredincluded pipe breaks and system misalignments involving the following tan ks and systems:Fire ProtectionRecycle Hold-up Tanks (RHTs)

Recycle MonitorTanks Reactor Make-up Water Storage Tanks (RMWSTs)Low-Pressure Service Water Nuclear Service Water Standby Shutdown Facility Standby Make-up PumpEquipment Decontamination Drinking Water Make-up Demineralized Water Heated Water Reactor Building Ventilation Cooling WaterBased on its review of the various potential dilution events, the licensee concluded that theworst-case dilution scenario is one initiated by a "continuous flow" event involving the break of a 4-inch pipe in the non-seismic fire protecti on system. The postulated break may be one due toseismic or tornado activity, and is based on a break size of approximately 1.5 in 2, which resultsin a maximum flow rate of 701 gpm of unborated water to the SFP. TS LCO (limiting condition for operation) 3.7.15 states "The spent fuel pool boron concentrationshall be within the limit specified in the COLR." In its boron dilution analysis the licensee assumed an initial SFP boron concentration of 2700 parts per million (ppm), which is theminimum boron concentration specified in the COLR. Based on the 2700 ppm initial pool boron concentration, a minimum starting pool volume of 374,403, gallons and an inflow of 701 gpm from the break of the fire protection line, the time required to dilute the pool to a boron concentration of 200 ppm, which corresponds to the K eff 0.95 safety limit was calculated to be32.36 hours1.5 days <br />0.214 weeks <br />0.0493 months <br />, and the total volume of water required for the dilution was over 1.3 million gallons.Since for the worst case dilution event it would take over 32 hours1.333 days <br />0.19 weeks <br />0.0438 months <br /> to dilute a SFP to theconcentration required to maintain K eff below 0.95 (200 ppm), and would involve substantialoverflow of a SFP, the licensee will have ample time to detect, identify, and mitigate the dilutionevent. Operators will receive numerous indicators to alert them long before 32 hours1.333 days <br />0.19 weeks <br />0.0438 months <br /> haveelapsed. Among the indicators would be SFP level Hi/Lo alarms, flooding in the auxiliarybuilding, and observations via shift rounds. The alarm response procedures direct operations to restore the SFP level to normal, and contain guidance for make-up to the SFP, and instructions for barriers to preclude adding sufficient unborated water to dilute boron concentration below the COLR minimum allowed concentration, and guidance on syst emalignment for adding boric acid to the SFP, should it be needed. Low-flow, long-term dilution events in which the rate of inleakage of unborated waterapproximately matches normal water loss can also result in dilution of the SFP boron concentration. However, because of the large quantity of water required to dilute the SFP boron concentration to the 200 ppm minimum, the leak would have to go undetected for several weeks. The plant TS, SR 3.7.15.1, requires that every 7 days the spent fuel pool boronconcentration be verified to be within the limits specified in the COLR. Therefore, low-flow long-term dilution events will be detected as a result of the plants' normal surveillance, asrequired by the plants' TSs.The licensee analyzed the boron dilution event involving system misalignment and determinedthe worst-case dilution from a finite-source system misalignment involved aligning the SFP cooling to take suction on the RMWST, and allowing the RHTs to piggyback on the RMWST.

The result of this misalignment event would be an introduction of just over 226,000 gallons of unborated water to a SFP, which is not a sufficient amount to dilute the pool boronconcentration below the 200 ppm safety limit. The licensee also determined that the worst-case dilution from an infinite-source misalignment results from aligning SFP cooling to take suction from nuclear service water. At a nominal rate of 140 gpm, the 200 ppm boron safety limit would be reached in just under 83 hours3.458 days <br />0.494 weeks <br />0.114 months <br />. Therefore this dilution case is bounded by the fire protection pipe break.The only credible scenario during a standby shutdown facility (SSF) event is for the SSFstandby make-up pump to take suction on a SFP for up to 72 hours3 days <br />0.429 weeks <br />0.0986 months <br /> for reactor coolant pump seal injection. After 72 hours3 days <br />0.429 weeks <br />0.0986 months <br /> the pump is secured, and the SFP make-up could occur using unborated water. The licensee determined that in the worst-case scenario the final concentration of the SFP water will be 1324 ppm boron which is well above the safety limit of200 ppm boron concentration. The licensee also indicated that since the SFP cooli ng syst emoperates at a higher pressure than the component cooli ng system, any dilution via SFP coolingheat exchanger leakage is not expected. The licensee has analyzed various potential dilution events and has concluded that unplannedand inadvertent events would not result in the dilution of a SFP to boron concentration less thanthat required to maintain K eff below 0.95. The NRC staff has reviewed the results of thelicensees boron dilution evaluations. The minimum concentration of boron required for the K effin a SFP remains below 0.95 and is assured based on the following*The flow rates associated with the dilution events

  • The large volume of water required for dilution
  • The long dilution times associated with the events
  • The SFP level detection alarms coupled with operator surveillance *Plant procedures to control SFP water level 3.2Criticality Analysis 3.2.1 Criticality Analysis Codes The code employed in the licensee's SFP criticality analysis is SCALE 4.4/KENO V.a. KENOV.a is a 3-D Monte Carlo criticality module in the SCALE 4.4 package. The licensee has performed a SCALE 4.4/KENO V.a benchmark analysis to determine calculational biases and uncertainties. The criticality analysis for the Catawba 1 and 2 new fuel storage vaults (NFVs) and SFPs hasbeen performed in accordance with the requirements of 10 CFR 50.68(b). This evaluation takes partial credit for soluble boron in the SFPs. The analysis determined that the Catawba 1 and 2 NFVs and SFPs can store unirradiated fuel up to 5 wt % U-235, with no location restrictions.The maximum 95/95 K eff for the NFV analysis was calculated to be 0.9324, meeting therequirements of 10 CFR 50.68(b)(2) and (3). For the Catawba 1 and 2 SFP criticality analyses, the maximum 95/95 K eff with no boron in theSFP was calculated to be 0.9680. This meets the no-boron 95/95 K eff < 1.0 criterion in10 CFR 50.68(b)(4). The SFP evaluation also confirmed that with 200 ppm of partial solubleboron credit, the maximum 95/95 K eff of 0.9294 remains well below the regulatory requirementthat the maximum 95/95 K eff be less than 0.95 for all normal conditions. The current minimum boron concentration required in the Catawba 1 and 2 SFPs (2700 ppm) isadequate to maintain the maximum 95/95 K eff below 0.95 for all credible accident scenarios inthe Catawba 1 and 2 SFPs.3.2.2 Bias and Uncertainty The NRC SFP criticality analysis guidance specifies that the maximum K eff value for thecriticality analysis should be the summation of the calculated nominal K eff, the bias in criticalityanalysis methods, manufacturing and calculational uncertainties, and the correction for the effect of the axial distribution in burnup when credit for burnup is taken. Uncertainties should be determined for the proposed storage facilities and fuel assemblies to account for tolerances inthe mechanical and material specifications. An acceptable method for determining the maximum reactivity may be either (1) a worst-case combination with mechanical and material conditions set to maximize K eff, or (2) a sensitivity study of the reactivity effects of tolerancevariations. If used, a sensitivity study should indicate all possible significant variations (tolerances) in the material and mechanical specifications of the racks; the results may bestatistically combined provided they are independent variations. Combinations of the two methods may also be used.The licensee has performed a SCALE 4.4/KENO V.a benchmark analysis of critical experimentsto determine calculational biases and uncertainties for both the 44-group and 238-group cross-section libraries included with the SCALE 4.4 package. For Catawba 1 and 2 criticality applications, the SCALE 4.4/KENO V.a method biases anduncertainties are based on analysis of 41 LEU critical experiments performed by Pacific Northwest Laboratories. These critical experiments model various square-pitch arrangements of fuel rods, and include both over- and under-moderated lattices. Because the NFV and SFP analyses model fresh fuel at only the highest permissible enrichment(5.00 +/- 0.05 wt % U-235), each of the 41 critical experiments selected was at the highestenrichment available (4.31 wt % U-235). The results from the benchmark analyses indicated that the 238-group cross-section libraryyields the more consistent results (i.e., smaller variations in reactivity bias) across the range of moderation in the selected critical experiments. Therefore, the 238-group cross-section library is used for all the SCALE 4.4/KENO V.a computations performed in the Catawba 1 and 2 NFV andSFPs criticality analyses. SCALE 4.4/KENO V.a modeling of these 41 critical experiments with the 238-group libraryyielded a benchmark calculational bias of +0.0061 k (average under-prediction of K eff) and anuncertainty of +/-0.0071 k. This bias and uncertainty are used in determining the total bounding 95/95 system K effs for each NFV or SFPs storage configuration. They were analyzed with SCALE 4.4/KENO V.a. and provide the results of the Catawba 1 and 2 NFV and SFPs criticalityevaluations, respectively.3.2.3 Computation of the Maximum 95/95 K effFor every fuel assembly design that is considered in the scope of the Catawba 1 and 2 SFPsand NFV criticality analyses, a nominal K eff is calculated. This K eff is only the base value,however. A total K eff is determined by adding several pertinent reactivity biases anduncertainties, to provide an overall 95-percent probability, at a 95-percent confidence level(95/95), that the true system K eff does not exceed the 95/95 K eff for that particular storagecondition. Table 4 in the licensee's September 13, 2005, application lists the various biases anduncertainties that are considered in the Catawba 1 and 2 NFV and SFPs criticality analyses.

Each of these biases and uncertainties is discussed in more detail below:

  • Benchmark Method BiasThis bias is determined from the benchmarking of the c ode system used (SCALE4.4/KENO V.a), and represents how much the code system is expected to over predict(negative bias) or under predict (positive bias) the "true K eff" of the physical system beingmodeled. The bias for SCALE 4.4/KENO V.a with its 238- group cross-section library is

+0.0061k.*Benchmark Method UncertaintyThis uncertainty is determined from the benchmarking of the code system used, and is ameasure of the expected variance (95/95 one-sided uncertainty) of predicted reactivity from the "true K eff" of the physical system being modeled. The method uncertainty forSCALE 4.4/KENO V.a, with its 238-group cross-section library, is +/-0.0071 k.*Monte Carlo Computational UncertaintyFor all the nominal SCALE 4.4/KENO V.a computations performed in this analysis todetermine 95/95 K effs, the Monte Carlo computational uncertainty is equal to 1.727*nominal. The nominal factor is the calculated standard deviation of k nominal (thenominal K eff for that particular case). The 1.727 multiplier is the one-sided 95/95tolerance factor for 1000 neutron generations. Each of the SCALE 4.4/KENO V.a cases in the SFP and NFV calculations counted 1000 neutron generations.

  • Mechanical UncertaintiesThe "mechanical uncertainty" represents the total reactivity uncertainty contributions ofvarious independent storage rack-related and fuel manufacturing-related mechanical uncertainty factors. These factors include reactivity effects for possible variations in fuel enrichment, fuel pellet diameter, fuel density, cladding dimensions, storage rack dimensions and material thickness tolerances, fuel assembly positioning within the storage cell, etc. The worst-case reactivity conditions are used for the nominal models in the Catawba 1 and 2 NFV evaluation; therefore, mechanical uncertainty factor needs tobe applied in the 95/95 K eff calculations for the NFV cases.The NRC staff has performed an independent evaluation of the licensee's analysis and reviewedthe uncertainties. Based on the review the NRC staff found the licensee's analysis acceptable. 3.3Compliance with 10 CFR 50.68(b) for the SFPs Licensees electing to comply with 10 CFR 50.68(b) must satisfy eight requirements. Thelicensee provided justification showing compliance with each of these requirements.Section 50.68(b)(1) requires that plant procedures prohibit the handling and storage at any onetime of more fuel assemblies than have been determined to be safely subcritical under the most adverse moderation conditions feasible with unborated water. The licensee provided information in the application that current plant provisions meet the requirements of 50.68(b)(1) for otheroperations involving movement and storage of spent and new fuel at the Catawba 1 and 2 sites.Section 50.68(b)(2) requires that the estimated ratio of neutron production to neutron absorptionand leakage (K eff) for the fresh fuel in the fresh fuel storage racks be calculated assuming theracks are loaded with fuel of the maximum fuel assembly reactivity and flooded with unboratedwater. The K eff must not exceed 0.95, 95/95 probability/confidence. Analyses by the licenseefor the Catawba 1 and 2 SFPs have determined that, for new fuel stored in a SFP, the K eff willbe less than 0.95, 95/95 probability/confidence.Section 50.68(b)(3) requires that the K eff not exceed 0.98, 95/95 probability/confidence, whenthe fuel storage racks are loaded with fresh fuel and filled with a low-density hydrogenousmaterial other than water. Analyses by the licensee for the Catawba 1 and 2 SFPs have determined that, for new fuel stored in the SFPs, the K eff will be less t han 0.95, 95/95probability/confidence levels.Section 50.68(b)(4) requires that if no credit is taken for soluble boron, the K eff of the spent fuelstorage racks not exceed 0.95, 95/95 probability/confidence, or if credit is taken for solubleboron that the K eff of the spent fuel storage racks not exceed 0.95, 95/95 probability/confidence,when flooded with borated water and the K eff remain below 1.0 (subcritical) if flooded withunborated water. Analyses by the licensee have shown that, for new fuel stored in the SFPs, the

K eff will be less than 0.95, 95/95 probability/confidence levels.Section 50.68(b)(5) requires that the quantity of special nuclear material (SNM) stored on site,other than nuclear fuel, be less than the quantity necessary for a critical mass. The licensee preforms a periodic inventory of SNM and will determine that the amount of non-fuel SNM storedat the Catawba 1 and 2 is very small and in a form which precludes criticality.Section 50.68(b)(6) requires the presence of radiation monitors at fuel storage and associatedhandling areas to detect excessive radiation levels and to initiate appropriate safety actions.

Area radiation monitors are permanently installed in selected areas throughout Catawba 1 and 2 including the new fuel storage area and on the SFP bridge crane. In locations that do not have permanently installed area radiation monitors, the licensee will utilize temporary gammasensitive monitors which will be required by procedure whenever fuel is being stored or handled. Section 50.68(b)(7) limits the maximum nominal U235 enrichment of fresh fuel to 5.0 percent byweight. TS section 4.3.1.2 restricts U235 enrichment of fresh fuel to less than 5.0 percent byweight. Section 50.68(b)(8) requires that the UFSAR be amended no later than the next update requiredby 50.71(e) to indicate that the licensee has chosen to comply with 50.68(b). The licensee has committed to make this change in the UFSAR update for Catawba 1 and 2.The NRC staff has reviewed the licensee's compliance with 10 CFR 50.68. With theimplementation of this amendment and the updating of the UFSAR the NRC staff finds thatCatawba 1 and 2 are in compliance with 10 CFR 50.68. 4.0

SUMMARY

The NRC staff has reviewed the licensee's proposed amendment and finds that adequate time isavailable for detection and mitigation of events capable of diluting the SFP from the SFP minimum soluble boron concentration of 2700 ppm per COLR per TS 3.7.15, to the minimum concentration of 200 ppm required to maintain k eff below 0.95. The methodology used wasfound to be consistent with the NRC staff-approved Westinghouse Owners Group genericmethodology for crediting soluble boron given in Topical Report WCAP-14416-P. The NRC stafffinds that the dilution requirements within 10 CFR 50.68, "Criticality accident requirements," andGDC 62, "Prevention of criticality in fuel storage and handling," are met. The NRC staff also finds that the proposed changes for the SFPs meet appropriate subcriticalityrequirements of 10 CFR 50.68 and GDC 62. In addition, the NRC staff finds that the licensee'samendment request provides reasonable assurance that under both normal and accident/upset conditions, that the licensee would be able to safely operate the plant and comply with the NRCregulations. The NRC staff has reviewed the changes to the TS Bases and finds they are consistent with thechanges to the TSs. The NRC staff finds the proposed changes to the TSs acceptable.

5.0 STATE CONSULTATION

In accordance with the Commission's regulations, the South Carolina State official was notifiedof the proposed issuance of the amendments. The State official had no comments.

6.0 ENVIRONMENTAL CONSIDERATION

The amendments change a requirement with respect to the installation or use of facilitycomponents located within the restricted area as defined in 10 CFR Part 20. The NRC staff hasdetermined that the amendments involve no significant increase in the amounts and nosignificant change in the types of any effluents that may be released offsite and that there is nosignificant increase in individual or cumulative occupational radiation exposure. The Commission has previously issued a proposed finding that the amendments involve no significant hazards consideration, and there has been no public comment on such finding (70 FR 70104). Accordingly, the amendments meet the eligibility criteria for categorical exclusion set forth in 10 CFR 51.22(c)(9). Pursuant to 10 CFR 51.22(b) no environmentalimpact statement or environmental assessment need be prepared in connection with the issuance of the amendments.

7.0 CONCLUSION

The Commission has concluded, based on the considerations discussed above, that: (1) thereis reasonable assurance that the health and safety of the public will not be endangered byoperation in the proposed manner, (2) such activities will be conducted in compliance with theCommission's regulations, and (3) the issuance of the amendments will not be inimical to thecommon defense and security or to the health and safety of the public.Principal Contributors: A. Stubbs F. Forsaty Date: September 27, 2006