Regulatory Guide 1.126: Difference between revisions

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{{Adams
{{Adams
| number = ML13350A271
| number = ML093360318
| issue date = 03/31/1977
| issue date = 03/31/2010
| title = an Acceptable Model and Related Statistical Methods for the Analysis of Fuel Densification
| title = an Acceptable Model and Related Statistical Methods for the Analysis of Fuel Densification.
| author name =  
| author name =  
| author affiliation = NRC/OSD
| author affiliation = NRC/RES
| addressee name =  
| addressee name =  
| addressee affiliation =  
| addressee affiliation =  
| docket =  
| docket =  
| license number =  
| license number =  
| contact person =  
| contact person = O'Donnell, Edward, RES/RGB
| document report number = RG-1.126
| case reference number = DG-1189
| document report number = RG-1.126, Rev. 2
| package number = ML093360304
| document type = Regulatory Guide
| document type = Regulatory Guide
| page count = 4
| page count = 10
}}
}}
{{#Wiki_filter:U.S. NUCLEAR REGULATORY  
{{#Wiki_filter:U.S. NUCLEAR REGULATORY COMMISSION
COMMISSION
March 2010
March 1977 REGULATORY  
Revision 2 REGULATORY GUIDE
GUIDE OFFICE OF STANDARDS
  OFFICE OF NUCLEAR REGULATORY RESEARCH
DEVELOPMENT
  The NRC issues regulatory guides to describe and make available to the public methods that the NRC staff considers acceptable for use in implementing specific parts of the agency
REGULATORY  
=s regulations, techniques that the staff uses in evaluating specific problems or postulated accidents, and data that the staff needs in reviewing applications for permits and licenses.  Regulatory guides are not substitutes for regulations, and compliance with them is not required.  Methods and solutions that differ from those set forth in regulatory guides will be deemed acceptable if they provide a basis for the findings required for the issuance or continuance of a permit or license by the Commission.
GUIDE 1.126 AN ACCEPTABLE  
 
MODEL AND RELATED STATISTICAL  
This guide was issued after consideration of comments received from the public.
METHODS FOR THE ANALYSIS OF FUEL DENSIFICATION
 
Regulatory guides are issued in 10 broad divisions C1, Power Reactors; 2, Research and Test Reactors; 3, Fuels and Materials Facilities; 4, Environmental and Siting; 5, Materials and Plant Protection; 6, Products; 7, Transportation; 8, Occupational Hea lth; 9, Antitrust and Financial Review; and 10, General.
 
Electronic copies of this guide and other recently issued guides are available through the NRC
=s public Web site under the Regulatory Guides document collection of the NRC
=s Electronic Reading Room at http://www.nrc.gov/reading-rm/doc-collections/ and through the NRC
=s Agencywide Documents Access and Management System (ADAMS) at http://www.nrc.gov/reading-rm/adams.html, under Accession No. ML09336031
 
===8. REGULATORY GUIDE===
1.126 (Draft was issued as DG-1189, dated December 2008)  AN ACCEPTABLE MODEL AND RELATED STATISTICAL METHODS FOR THE ANALYSIS OF FUEL DENSIFICATION  


==A. INTRODUCTION==
==A. INTRODUCTION==
and C.2 of this guide is not intended to supersede NRC-approved vendor models.Appendix K. "ECCS Evaluation Models," to 10 CFR Part 50, "Licensing of Production and Utilization The statistical methods (SectionC-.3).  
This guide describes an analytical model and related assumptions and procedures that the staff of the U.S. Nuclear Regulatory Commission (NRC) considers acceptable for predicting the effects of fuel densification in light-water-cooled nuclear power reactors.  To meet these objectives, the guide describes statistical methods related to product sampling that will ensure that this and other approved analytical models will adequately describe the effects of densification for each initial core and reload fuel quantity produced.
measurement Facilities," requires that the steady-state temperature methods (Section C.4), and istarooy assumptions distribution and stored energy in the fuel before a hypo- (Section C.5) are compatible wtth models.thetical loss-of-coolant accident (LOCA) be calculated, Therefore Sections C.3. C-.;,aJid:`;c.5 co ild be applied taking fuel densification into consideration.
 
The regulatory framework that the NRC has established for nuclear power plants consists of a number of regulations and supporting guidelines, including General Design Criterion 10, "Reactor Design," as set forth in Appendix A, "General Design Criteria for Nuclear Power Plants," to Title 10, Part 50, "Domestic Licensing of Production and Utilization Facilities," of the Code of Federal Regulations (10 CFR Part 50) (Ref. 1). Specifically, Appendix K, "ECCS Evaluation Models," to 10 CFR Part 50 requires that the steady-state temperature distribution and stored energy in the fuel before a hypothetical loss-of-coolant accident (LOCA) be calculated, taking fuel densification into consideration.
 
Rev. 2 of RG 1.126, Page 2 This regulatory guide contains information collection requirements covered by 10 CFR Part 50 that the Office of Management and Budget (OMB) approved under OMB control number 3150-0011.  The NRC may neither conduct nor sponsor, and a person is not required to respond to, an information collection request or requirement unless the requesting document displays a currently valid OMB control number.
 
==B. DISCUSSION==
In-reactor densification (shrinkage) of oxide fuel pellets affects fuel temperatures in several ways-(1) gap conductance may be reduced because of the decrease in pellet diameter, (2) the linear heat generation rate is increased because of the decrease in pellet length, and (3) the decrease in pellet length may cause gaps in the fuel column and may produce local power spikes and the potential for cladding collapse.  Dimensional changes in pellets in the reactor do not appear to be isotropic, so axial and radial pellet dimension changes will be treated differently. Furthermore, items (1) and (2) above are single-pellet effects, whereas item (3) is the result of simultaneous changes in a large number of pellets.  These distinctions must be considered in applying analytical models.
 
The NRC staff has reviewed the available information concerning fuel densification.  NUREG-0085, "The Analysis of Fuel Densification," issued July 1976, contains the technical basis for the regulatory position of this guide (Ref. 2).  The model presented in Sections C.1 and C.2 of this guide is not intended to supersede NRC-approved vendor models.
 
The statistical methods (Section C.3), measurement methods (Section C.4), and isotropy assumptions (Section C.5) are compatible with most vendor models.  Therefore Sections C.3, C.4, and C.5 could be applied to densification models that differ from the one presented in Sections C.1 and C.2.


This to densitication models the one pre-guide provides an analytical model and related assump- sented in Sect ins.Q.-i 'nd C2;, " tions and procedures that are acceptable to the NRC staff for predicting thle effects of fuel densification in light-water-cooled nuclear power reactors.
Rev. 2 of RG 1.126, Page 3


The guide C REGU.iATORY
==C. REGULATORY POSITION==
POSITION also describes statistical methods related to product sampling that will provide assurance that this and li.-Maximum iDisification other approved analytical models will adequately de-scribe the effects of densification for each initial core" -:-, .The; density of a fuel pellet* in the reactor increases and reload fuel quantity produced.
1. Maximum Densification The density of a fuel pellet
1 in the reactor increases with burnup and achieves a maximum value at a relatively low burnup (generally less than 10,000 megawatt days per metric ton (MWd/t)).  For analytical purposes, this maximum density minus the initial density (i.e., the maximum density change) is assumed to be the same as the density change that would occur outside the reactor in the same pellet during resintering (sntr) at 1700 °C (3092 °F) for 24 hours:
2.  Where the ex-reactor resintering results in a negative density change (i.e., swelling), zero in-reactor densification should be assumed.


,.... witA. burnup and achieves a maximum value at a rela--tively low burntip (generally
2. Densification Kinetics For pellets that have a resintering density change sntr of less than 4 percent of theoretical density (TD), the in-reactor density change  as a function of burnup (BU) may be taken as the following:
< 10,000 M\Yd/t U). For
      = 0    (for BU  20 MWd/t);
    = m log (BU) + b    (for 20 < BU < 2000 MWd/t); and      = sntr    (for BU  2000 MWd/t),  where the coefficients m and b are given by
    0 = m log (20) + b and    sntr = m log (2000) + b.


==B. DISCUSSION==
For pellets exhibiting a resintering density change in excess of 4-percent TD, the in-reactor density change as a function of burnup may be taken as the following:
analytical purposes, this maximum density minus the initial density. i.e., the maximum density change,* In-reactor densification (shrinkage)','of oxide Iitel is assumed to be the same as the density change Asntr pellets affects fuel temperatures in ste..ral '0*ys: (1) that would occur outside the reactor in the same gap conductance may be reduced beca f''6rthe de- pellet during resintering at I 700&deg;C for 24 hours.0 crease in pellet uiameter;.
      = 0   (for BU  5 MWd/t);  
1 t),) me linear neat generation rate is increased decrease in pellet length;and (3) the pellet-le' .d'teases may cause gaps in the fuel colur id n, prMce local power spikes and the pot ial c ing collapse.
    = m log (BU) + b    (for 5 < BU < 500 MWd/t); and      = sntr    (for BU  500 MWd/t),                                          
1 The model presented in this guide is applicable to UO
2, UO 2-PuO 2, and UO 2-Gd 2 O 3 fuel pellets.
 
2 The Terms of Equations at the back of this guide defines some of the terms and symbols used in this document.


Dimensional changes i Il11ets in lie reactor do not appear to be, a radial pellet dimension changes will b ted "clferently.
Rev. 2 of RG 1.126, Page 4 where the coefficients m and b are given by
    0 = m log (5) + b and    sntr = m log (500) + b.


Furthermore, items (1) and (2) abo i;re single-pellet effects, whereas item (3)is the result of simultaneous changes in a large number of pellets. These distinctions must be taken into account in applying analytical models.The NRC staff has reviewed the available information concerning fuel densification, and the technical basis for the Regulatory Position of this guide is given in Reference
In applications of these equations, sntr will have the value
1. The model presented in Sections C.I Where the ex-reactor resintering results in a negative density change (i.e.. swelling), zero in-reactor densifi-cation should le assumed.2. Densifieation Kinetics For pellets that have a resintering density change Asntr of less than 4% of theoritical density (TD), the in-reactor density change Ap -1% a function of burnup BU may be taken as***The model presented in this guide is applicahle only to U0 2 fuel pellets.*&Symbols are defined in the List of Symtols at the back of this guid
*sntror **sntr, which will be described in Section C.3. The burnup unit MWd/t in the above expressions is megawatt days per metric ton of heavy metal (uranium or uranium plus plutonium in mixed-oxide (MOX) fuels).
3. Statistical Methods To apply the above model or any densification model that depends on an ex-reactor resintering density change, a random sample of the pellet population of interest should be resintered. Resintering the pellets in the sample will result in a set of density changes sntr. Several characteristics of these values are needed to complete the densification analysis.


====e. USNRC REGULATORY ====
The population of analytical interest may be composed of subsets of pellets from either a single material population or a group of material populations. A "material population" is defined as a group of pellets manufactured from a single powder source under the same range of fabricating conditions in such a manner that the pellets exhibit consistent resintering behavior.  For those subsets taken from material populations that exhibit consistent resintering behavior, the sample data from the material population taken as a whole may be used to characterize the densification behavior of the subsets.
GUIDES Reggulatory Guide% wte issuerd to desribe ant make available to the public methods acieptable to the NRC stail of implementing speeilic paris of the Commission's tegufations, to delineate techniqtur$
used by the %tsalI in evaluating poecifIic litottlern of rostulated accidents, or to provide guidance to applicants, Regulatory Guides awe not subltitutes lot regublions, arnd commlhince with them is tot required.Methods and solutions dilferent from those set Out in the guides will be accept-able If they provide a basis for the findings requisite to the issuance or continuance of a permit or license by the Commission, Comments and suggestions for improvements in these guides rt- encouraged at all times, and guides wtil bit revised, A ,tprotriatle.


to accommodate comments and to tretect new Information or experience.
3.1 Single-Pellet Effects Analyses of the effect of densification on stored energy and linear heat generation rate must account for pellets that have the greatest propensity for densification.  To accomplish this with a resintering-based model such as that described in Sections C. 1 and C.2, a resintering density change value **sntrthat conservatively bounds 95 percent of the population sntr values with 95-percent confidence should be used.  The population of analytical interest is the initial core loading or reload quantity of fuel for which the safety analysis, and hence the densification analysis, is being performed, and this population may be composed of subsets from a number of material populations.  Once the material populations and their respective contributions (i.e., subsets) to the population of analytical interest are determined, random sampling procedures may be used to characterize the resulting population.  When random sampling of the resulting population is not feasible, a conservative characterization may be obtained by using the largest of the characterizations of the contributing subsets.


However. comments on this guideif I eceived within about two months alter its i-.suanca.
1  If the distribution of sntr values of a population is normal, methods of evaluating normally distributed data may be used. If the "W" test or D' test (when 50 or more data points are used) (Ref. 3) demonstrates nonnormality at the 1-percent level of significance, nonparametric statistical methods should be used unless a different functional form can be satisfactorily justified to describe the distribution of the sntr value


will fe tParticularly useful In evaluating the neate for an early reviston.Conmments should be ent 1o thi, Secretary of tI!
====s. Thus ====
US. Nucleiar  latury Commitsion.
**sntr is the upper one-sided 95/95 tolerance limit for the density changes and can be obtained from the sample values using one of the methods outlined belo


Wsiir'nton, O.C. 70555, Attention- Dorcketrrg and Servly Branch.The guides are in ttte following ten rlwvivions t. Power Reactors 6. PelXjucls 2. Research and Te'st Reactors
====w.     ====
1 It is incorrect to prorate the characterizations of the contributing subsets by computing weighted averages over the subsets.


===7. Ttantrurtatiun===
Rev. 2 of RG 1.126, Page 5 3.1.1 Normal Distribution In this case, **sntris given by the following:
3. Fuellsant Materials Facilities
    **sntr = sntr + c's,  where sntr is the mean of the sample data, s is the standard deviation of the sample data, and c' is given in Table 1 (from Ref. 4).  
8, Occupational IHealth 4. Environmental aontSiting
Table 1  Values To Be Used for c' To Determine
9. Antitrust tlevew.S. Materials and Plant Protection t0. Geriryal RectueSts fat single covies Ol isisuo guides ferhich rmnay' tie eprodur.ced at tto* ;iace-ment on an automatic dititl)ution list for sing 1 le copies of future f tidus in streciftc divisions should be madte in writing to the US. Nuclear Regutlarnrv Cnnmission, Washington, D.C. 70555, Attention:  
**sntr with Normal Distribution Number of Observationsc' 4 5.15 5 4.20 6 3.71 7 3.40 8 3.19 9 3.03 10 2.91 11 2.82 12 2.74 15 2.57 20 2.40 25 2.29 30 2.22 40 2.13 60 2.02 100 1.93 200 1.84 500 1.76 1.64  3.1.2 Nonnormal Distribution In this case, **sntris given by the following:  
Ditector.
    **sntr = )(m sntr,  where )(m sntr is the m th largest sntr value in a ranking of the observed values of sntr from the sample.  The integer m depends on the sample size according to Table 2 (from Ref. 5).  


Division o t Document Crontfrol.
This method requires a minimum of 60 observations to produce a meaningful result.


I .Ap=O0 (for BU < 20 NIWd/tU);S (for 20 < BU < 2000 NtWd/tU);(la)(I b)(Ic)and ,, = APsntr (for BU > 2000 MWd/tU), where tile coefficients m and b are given by 0 = m log(20) + b and'Psntr = i log(2000)
Rev. 2 of RG 1.126, Page 6 Table 2 Values To Be Used for m To Determine
+ b.For pellets exhiibiting a resintering density change in excess of 4% TD. the in-reactor density change as a function burnup may be taken as ating normally distributed data may be used. If the"W" test (Ref. 2) demonstrates nonnormality at the -1%level of significance.
**sntr with Nonnormal Distribution Number of Observations m 50 - 55 - 60 1 65 1 70 1 75 1 80 1 85 1 90 1 95 2 100 2 110 2 120 2 130 3 140 3 150 3 170 4 200 5 300 9 400 13 500 17 600 21 700 26 800 30 900 35 1000 39  3.2 Multiple-Pellet Effects Average pellet behavior determines changes in fuel column length, which can result in axial gaps in the pellet stack. In this case, however, the population to be considered is not the core or reload quantity characterized above, but rather the material population (or subset thereof) within that quantity that exhibits the largest mean of the sntrvalues from the sample.  The distribution of sntrvalues for the selected material population may be assumed to be normal.


nonparametric statistical methods should be used unless a different functional form can be satisfactorily justified to describe the distribution of the LAsntr values. Thus 6sAnptr is tile upper one.sided 95/95 tolerance limit for the density changes and can be obtained from the sample values using one of the methods outlined below.(1) NormalDistribution.
To analyze effects related to column-length changes, resintering-based densification models should use a density change value
*sntrthat bounds the selected material population mean with 95-percent confidence. Thus, *sntris the upper one-sided 95-percent confidence limit on the mean 


In this case, Ps*nr is given by ASiltr = Epsnir + C's.wherce -'Nsntr is tile mean of the sample data, s is the standard deviation of tile sample data, and c' is given in Table I (from Ref. 3).Lp =0 (forhBU 5 MWd/tU): Ap = m log(BU) + b (for 5 < BU < 500 MWd/tU): and -P -APsntr (for BU > 500 MWd/tU), where the coefficients m and b are given by 0 = m log(S) + b and ,Psntr = m log(500) + b.(2a)(21b )GOc TABLE I VALUES TO BE USED FOR c'TO DETERMINE
Rev. 2 of RG 1.126, Page 7 density change and can be obtained from the sample values using the following expression:
64lr WITH NORMAL DISTRIBUTION
    *sntr = sntr'+ cs',  where sntr'is the mean of the sample data from the selected material population, s' is the standard deviation of the sample data from the selected material population, and c is given in Table 3 (from Ref. 4). Table 3 Values To Be Used for c To Determine
Number of Observations c In applications of Equations I and 2, ,Psntr will have tile value st**r or tmntr. which will be described in Section C.3. The burnup unit MWd/tU in the above expressions is megawatt days per metric ton of heavy metal (uranium).
*sntr  Number of Observations c 4 1.18 5 0.95 6 0.82 7 0.73 8 0.67 9 0.62 10 0.58 11 0.55 12 0.52 15 0.45 20 0.39 25 0.34 30 0.31 40 0.27 60 0.22 100 0.17 200 0.12 500 0.07 0  4. Measurement Methods To measure the density change sntr during resintering, either geometric or true densities may be used, so long as the same method is used before and after resintering.  Techniques such as vacuum impregnation/water immersion, mercury immersion, gamma-ray absorption, and mensuration are acceptable.  It is also acceptable to infer the density change from a diameter change, using the isotropic relation /sntr = 3 D D sntr/, where sntr D is the diameter change experienced during resintering.
3. Statistical Methods To apply tile above model or any densification model that depends on an ex-reactor resintering density change, a random sample of the pellet population of interest must be resintered.


Resintering the pellets in the sample will result in a set of density changes 6Psntr. Several characteristics of these values are needed to complete the densification analysis.a. Single-Pellet Effects Analyses of the effect of densification on stored energy and linear heat generation rate must account for pellets that have the greatest propensity for densifica.
Resintering should be performed in a furnace with a known temperature distribution in the working region. Temperatures during resintering should be measured using either thermocouples or calibrated optical methods with established blackbody conditions. Furnace temperatures should be maintained so that specimen temperatures are no lower than the desired test temperature (1700 &deg;C or 3092 &deg;F for 24 hours in the model above) after temperature measurement errors have been taken into account.


tion. To accomplish this with a resintering-based model such as that described in Sections C.1 and C.2, a re-sintering density change value Apjn*tr that conservative- ly bounds 95% of the population APsntr values with 95% confidence should be used. The population of interest is the initial core loading or. reload quantity of fuel for which the safety analysis, and hence the den-sification analysis, is being performed.
Rev. 2 of RG 1.126, Page 8 In considering fuel stoichiometry, an oxygen-to-metal ratio of approximately 2.00 should be maintained. This may be accomplished by using dry tank hydrogen or dry gas mixtures (e.g., N
2-H 2) and avoiding temperatures in excess of about 1800 &deg;C (3272 &deg;F).
5. Isotropy Assumptions To use predicted density changes in a calculation of the effects of in-reactor densification, it is necessary to make some assumption about the isotropy of fuel densification.  For changes in pellet diameter D, isotropic densification may be assumed, so that D/D = /3.  For changes in pellet or fuel column length L, anisotropic densification is assumed such that L/L = /2. For further discussion of the conservative nature of these assumptions, see Section III. D of NUREG-008


If the distri-bution of values is normal, methods of evalu.4 5 6 7 8 9 10 11 12 is 20 25 30 40 60 100 200 500 00 5.15 4.20 3.71 3.40 3.19 3.03 2.91 2.82 2.74 2.57:.40 2.29 2.2 2 2.13 2.02 1.93 1.84 1.76 1.64 (2)given by NonnormalDistribution.
===5.     ===


In this case Apntis Ap~t t where P is the mth largest 5Psntr value in a ranking ot the observed values o0 6Psntr from the sample.The integer m depends on tile sample size according to Table 2 (from Ref. 4).1.126-2 TABLE 2 VALUES TO BE USED FOR m TO DETERMINE
==D. IMPLEMENTATION==
WITH NONNORMAL
The purpose of this section is to provide information to applicants and licensees regarding the NRC's plans for using this regulatory guide. The NRC does not intend or approve any imposition or backfit in connection with its issuance.
DISTRIBUTION
Number of Observations
50 55 60 65 70 75 80 85 90 95 100 110 120 130 140 15o 170 200 300 400 500 600 700 800 900 1000 m 2 3 3 3 4 5 9 13 17 21 26 30 35 39 where 'P;sntr is the mean of t(ie sample data from the selected lot, s' is the standard deviation of the sample data from the selected lot, and c is given in Table 3 (from Ref. 3).TABLE 3 VALUES TO BE USED FOR c TO DETERMNINE
i.snir Number of Observations C 4 6 7 8 9 10 I I 12 20 25 30 40 60 100 200 500 1.18 0.95 0.82 0.73 (0.67 0.62 0.58 0.55 0.52 0.45 0.39 0.34 0.31 0.27 0.-2 0.17 0.12 0.07 0 4. Measurement Methods Note that a minimum of 60 observations is required to produce a meaningful result by this method.b. Multiple-Pellet Effects Fuel-column.length changes, which can result in axial gaps in the pellet stack, are determined by average pellet behavior.


In this case, however, the population to be considered is not the core or reload quantity characterized above, but rather the pellet lot within that quantity that exhibits the largest mean of the 6,sntr values from the sample. A pellet lot is defined as a group of pellets made from a single UOi powder source that has been processed under the same condi-tions. The distribution of 6Psntr values for the selected pellet lot is assumed to be normal. To analyze effects related to column-length changes. resintering-based densification models should use a density change valuethat bbunds the selected pellet lot mean with 95% confidence, Thus ,'s'ntr is the upper one-sided 95% confidence limit on the mean density change and can be obtained from the sample values using the expres-sion: APs 4 ntr ="Psntr + cs'To measure the density change A, sntr during resin-tering, either geometric or true densities may he used, so long as the same method is used before and after resin.tering. Techniques such as vacuum impregnation/
In some cases, applicants or licensees may propose or use a previously established acceptable alternative method for complying with specified portions of the NRC's regulations. Otherwise, the methods described in this guide will be used in evaluating compliance with the applicable regulations for license applications, license amendment applications, and amendment requests.
water immersion, mercury immersion, gamnta.r-ay ab-sorption.


and mensuration ate acceptable.
Rev. 2 of RG 1.126, Page 9 TERMS USED IN EQUATIONS
The following identifies the major symbols used in Section C: 
BU burn up unit expressed in megawatt days per metric ton of heavy metal (MWd/t)
c, c' population parameters in Tables 1 and 3


It is also acceptable to infer the density change from a diameter change. using the isotropic relation "Psnir/o =3LDsntr/D.
D nominal initial pellet diameter, centimeters (cm)
L nominal fuel column length, cm m population parameter from Table 2


where ADsntr is the diameter change exper-ienced during resintering.
s standard deviation of the sample data s' standard deviation of the sample data from the selected material population


Resintering should be performed in a laboratory- quality furnace with a known temperature distribution, in the working region. Temperatures during resintering should be measured using either thermocouples or calibrated optical methods with established black-body conditions.
TD theoretical density, grams per cubic centimeter (g/cm
3)  D in-reactor pellet diameter change (function of burnup), cm sntr D measured diameter change of a pellet resulting from ex-reactor resintering, cm L in-reactor fuel column length change (function of burnup), cm in-reactor pellet density change (function of burnup), g/cm
3  sntr measured density change of a pellet resulting from ex-reactor resintering, g/cm
3  sntr  mean of the measured density change data, sntr, g/cm 3  sntr' mean of a selected material population of the measured density data, sntr, g/cm 3  *sntr one-sided 95-percent upper confidence limit on the mean of the sntr values from the selected material population, g/cm
3  **sntr one-sided 95/95 upper tolerance limit for the total population of sntrvalues, g/cm
3  nominal initial pellet density, g/cm
3 Rev. 2 of RG 1.126, Page 10
REFERENCES
1  1. 10 CFR Part 50, "Domestic Licensing of Production and Utilization Facilities," U.S. Nuclear Regulatory Commission, Washington, DC.


Furnace temperatures should be so maintained that true specimen temperatures are no lower than the desired test temperature
2. NUREG-0085, "The Analysis of Fuel Densification," R.0. Meyer, U.S. Nuclear Regulatory Commission, Washington, DC, July 1976.
(1700'C in the model above) after temperature measurement errors have been taken into account.Fuel stoichiometry (O/M ,; 2.00) should be main-tained by using dry tank hydrogen or dry gas mixtures (e.g.. N2-H2) and avoiding temperatures in excess of-1800&deg;eC.0 1.126-3
5. Isotropy Assumptions In order to use predicted density changes in a cal-culation of the effects of inTreactor densification, it is necessary to make some assumlplion about tile isotropy of' fuel densification.


For ch: ages in pellet diameter D. isotropic densilication may be assumed, so that ,:I)/D = .Ap/3p. For changes in pellet or fuel column leigth L. anisolropic densification is assumed such that -./L =Ar.1 2,o.
3. ANSI Standard N15.15-1974, "Assessment of the Assumption of Normality (Employing Individual Observed Values)," American National Standards Institute.


==D. IMPLEMENTATION==
2  4. G.J. Hahn, "Statistical Intervals for a Normal Population, Part I. Tables, Examples and Applications," J. Quality Technol. 2, 115, 1970.
The purpose of this section is to provide information to applicants and licensees regarding the NRC" staft's plans for using this regulatory guide.This guide reflects a relinement in NRC( practice and supersedes the previously accepted assumption that all fuels densify to a maximum density of 9thi.5'; of tineir theoretical density as measured geometrically.


Except iim those cases in which the applicant proposes an accept-able alternative method for complying with specified portions of the Commission's regulations,.  
5. P.N. Somerville, "Tables for Obtaining Non-Parametric Tolerance Limits," Ann. Math. Stat. 29, pp. 599-601, 1958.
the method described herein will be used in the evaluation of sub.mittals for construction permit, operating license, and reload applications docketed after November I. 1977.unless this guide is revised as a result of suggestions from the public or additional staff review. If for any reason the effects of' fuel densification are reanalyzed for fuel covered in an applicalion docketed on tir before No-vember 1. 1977. the method described in this guide would not be necessary and previously approved assunmp-tions would he allowed for that fuel.If an applicant wishes to use this regulatory guide in developing submittals for applications docketed on or before November 1. 1977. the pertinent portions of the application will be evaluated on ihe basis of1 this guid


====e. REFERENCES====
1  Publicly available NRC published documents such as Regulations, Regulatory Guides, NUREGs, and Generic Letters  listed herein are available electronically through the Electronic Reading Room on the NRC's public Web site at:
1. R. 0. Meyer. ""rhe Anakysis of Fuel Densi-fication." USNRC Report NURIFG-005.
http://www.nrc.gov/reading-rm/doc-collections/. Copies are also available for inspection or copying for a fee from the  NRC's Public Document Room (PDR) at 11555 Rockville Pike, Rockville, MD; the mailing address is USNRC PDR,  Washington, DC 20555; telephone 301-415-4737 or (800) 397-4209; fax (301) 415-3548; and e-mail


July 1976.2. "American National Standard Assessment of' the Assumnption of' Normnality (Emploving Ind ividu;,I Ob-served Values)'" ANSI Standard NI 5.15-19 74.3. G. J. Hahn. "Statistical Intervals for a Normal Pop-ulation. Part I. Tables, Examples and Applications," J. Quality Technol. 115 (1970), 4, P. N. Somerville. "Tables for Obtaining Non.Para-metric Tolerance Limits." Ann. Math. Stat. 29, 559 (1958).LIST OF SYMBOLS T'he major symbols used in Sections C.I through C.5 are identified below: BU iHurnup. %IWdjtU.D Nominal initial pellet diameter, cni.I, Nominal initial pellet length, cm.TI) Theoretical density, g/cm 3.A 1) In-reactor pellet diameter change (function of burnup). cm.ADsntr Measured diameter change of a pellet due to ex-reactor resintering, cm.A t. In-reactor pellet length change (function of hurnup), cm.A, In-reactor pellet density change (function of burnup), g/cm 3.APsntr Measured density change of a pellet due to ex-reactor resintering, g/cm 3.s.ntr One-sided
PDR.Resource@nrc.gov.  2 Copies of the non-NRC documents included in these references may be obtained directly from the publishing  organization.}}
95% upper confidence limit on, the mean of tile A0sntr values from the selected lot. g/cm 3.A 0 *n*r One-sided
95/95 upper tolerance limit for the total population of tLsntr values, g/cm 3.P Nominal initial pellet density, g/cm 3.1,126-4}}


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Revision as of 18:50, 19 September 2018

an Acceptable Model and Related Statistical Methods for the Analysis of Fuel Densification.
ML093360318
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Issue date: 03/31/2010
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References
DG-1189 RG-1.126, Rev. 2
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U.S. NUCLEAR REGULATORY COMMISSION

March 2010

Revision 2 REGULATORY GUIDE

OFFICE OF NUCLEAR REGULATORY RESEARCH

The NRC issues regulatory guides to describe and make available to the public methods that the NRC staff considers acceptable for use in implementing specific parts of the agency

=s regulations, techniques that the staff uses in evaluating specific problems or postulated accidents, and data that the staff needs in reviewing applications for permits and licenses. Regulatory guides are not substitutes for regulations, and compliance with them is not required. Methods and solutions that differ from those set forth in regulatory guides will be deemed acceptable if they provide a basis for the findings required for the issuance or continuance of a permit or license by the Commission.

This guide was issued after consideration of comments received from the public.

Regulatory guides are issued in 10 broad divisions C1, Power Reactors; 2, Research and Test Reactors; 3, Fuels and Materials Facilities; 4, Environmental and Siting; 5, Materials and Plant Protection; 6, Products; 7, Transportation; 8, Occupational Hea lth; 9, Antitrust and Financial Review; and 10, General.

Electronic copies of this guide and other recently issued guides are available through the NRC

=s public Web site under the Regulatory Guides document collection of the NRC

=s Electronic Reading Room at http://www.nrc.gov/reading-rm/doc-collections/ and through the NRC

=s Agencywide Documents Access and Management System (ADAMS) at http://www.nrc.gov/reading-rm/adams.html, under Accession No. ML09336031

8. REGULATORY GUIDE

1.126 (Draft was issued as DG-1189, dated December 2008) AN ACCEPTABLE MODEL AND RELATED STATISTICAL METHODS FOR THE ANALYSIS OF FUEL DENSIFICATION

A. INTRODUCTION

This guide describes an analytical model and related assumptions and procedures that the staff of the U.S. Nuclear Regulatory Commission (NRC) considers acceptable for predicting the effects of fuel densification in light-water-cooled nuclear power reactors. To meet these objectives, the guide describes statistical methods related to product sampling that will ensure that this and other approved analytical models will adequately describe the effects of densification for each initial core and reload fuel quantity produced.

The regulatory framework that the NRC has established for nuclear power plants consists of a number of regulations and supporting guidelines, including General Design Criterion 10, "Reactor Design," as set forth in Appendix A, "General Design Criteria for Nuclear Power Plants," to Title 10, Part 50, "Domestic Licensing of Production and Utilization Facilities," of the Code of Federal Regulations (10 CFR Part 50) (Ref. 1). Specifically, Appendix K, "ECCS Evaluation Models," to 10 CFR Part 50 requires that the steady-state temperature distribution and stored energy in the fuel before a hypothetical loss-of-coolant accident (LOCA) be calculated, taking fuel densification into consideration.

Rev. 2 of RG 1.126, Page 2 This regulatory guide contains information collection requirements covered by 10 CFR Part 50 that the Office of Management and Budget (OMB) approved under OMB control number 3150-0011. The NRC may neither conduct nor sponsor, and a person is not required to respond to, an information collection request or requirement unless the requesting document displays a currently valid OMB control number.

B. DISCUSSION

In-reactor densification (shrinkage) of oxide fuel pellets affects fuel temperatures in several ways-(1) gap conductance may be reduced because of the decrease in pellet diameter, (2) the linear heat generation rate is increased because of the decrease in pellet length, and (3) the decrease in pellet length may cause gaps in the fuel column and may produce local power spikes and the potential for cladding collapse. Dimensional changes in pellets in the reactor do not appear to be isotropic, so axial and radial pellet dimension changes will be treated differently. Furthermore, items (1) and (2) above are single-pellet effects, whereas item (3) is the result of simultaneous changes in a large number of pellets. These distinctions must be considered in applying analytical models.

The NRC staff has reviewed the available information concerning fuel densification. NUREG-0085, "The Analysis of Fuel Densification," issued July 1976, contains the technical basis for the regulatory position of this guide (Ref. 2). The model presented in Sections C.1 and C.2 of this guide is not intended to supersede NRC-approved vendor models.

The statistical methods (Section C.3), measurement methods (Section C.4), and isotropy assumptions (Section C.5) are compatible with most vendor models. Therefore Sections C.3, C.4, and C.5 could be applied to densification models that differ from the one presented in Sections C.1 and C.2.

Rev. 2 of RG 1.126, Page 3

C. REGULATORY POSITION

1. Maximum Densification The density of a fuel pellet

1 in the reactor increases with burnup and achieves a maximum value at a relatively low burnup (generally less than 10,000 megawatt days per metric ton (MWd/t)). For analytical purposes, this maximum density minus the initial density (i.e., the maximum density change) is assumed to be the same as the density change that would occur outside the reactor in the same pellet during resintering (sntr) at 1700 °C (3092 °F) for 24 hour2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br />s:

2. Where the ex-reactor resintering results in a negative density change (i.e., swelling), zero in-reactor densification should be assumed.

2. Densification Kinetics For pellets that have a resintering density change sntr of less than 4 percent of theoretical density (TD), the in-reactor density change as a function of burnup (BU) may be taken as the following:

= 0 (for BU 20 MWd/t);

= m log (BU) + b (for 20 < BU < 2000 MWd/t); and = sntr (for BU 2000 MWd/t), where the coefficients m and b are given by

0 = m log (20) + b and sntr = m log (2000) + b.

For pellets exhibiting a resintering density change in excess of 4-percent TD, the in-reactor density change as a function of burnup may be taken as the following:

= 0 (for BU 5 MWd/t);

= m log (BU) + b (for 5 < BU < 500 MWd/t); and = sntr (for BU 500 MWd/t),

1 The model presented in this guide is applicable to UO

2, UO 2-PuO 2, and UO 2-Gd 2 O 3 fuel pellets.

2 The Terms of Equations at the back of this guide defines some of the terms and symbols used in this document.

Rev. 2 of RG 1.126, Page 4 where the coefficients m and b are given by

0 = m log (5) + b and sntr = m log (500) + b.

In applications of these equations, sntr will have the value

  • sntror **sntr, which will be described in Section C.3. The burnup unit MWd/t in the above expressions is megawatt days per metric ton of heavy metal (uranium or uranium plus plutonium in mixed-oxide (MOX) fuels).

3. Statistical Methods To apply the above model or any densification model that depends on an ex-reactor resintering density change, a random sample of the pellet population of interest should be resintered. Resintering the pellets in the sample will result in a set of density changes sntr. Several characteristics of these values are needed to complete the densification analysis.

The population of analytical interest may be composed of subsets of pellets from either a single material population or a group of material populations. A "material population" is defined as a group of pellets manufactured from a single powder source under the same range of fabricating conditions in such a manner that the pellets exhibit consistent resintering behavior. For those subsets taken from material populations that exhibit consistent resintering behavior, the sample data from the material population taken as a whole may be used to characterize the densification behavior of the subsets.

3.1 Single-Pellet Effects Analyses of the effect of densification on stored energy and linear heat generation rate must account for pellets that have the greatest propensity for densification. To accomplish this with a resintering-based model such as that described in Sections C. 1 and C.2, a resintering density change value **sntrthat conservatively bounds 95 percent of the population sntr values with 95-percent confidence should be used. The population of analytical interest is the initial core loading or reload quantity of fuel for which the safety analysis, and hence the densification analysis, is being performed, and this population may be composed of subsets from a number of material populations. Once the material populations and their respective contributions (i.e., subsets) to the population of analytical interest are determined, random sampling procedures may be used to characterize the resulting population. When random sampling of the resulting population is not feasible, a conservative characterization may be obtained by using the largest of the characterizations of the contributing subsets.

1 If the distribution of sntr values of a population is normal, methods of evaluating normally distributed data may be used. If the "W" test or D' test (when 50 or more data points are used) (Ref. 3) demonstrates nonnormality at the 1-percent level of significance, nonparametric statistical methods should be used unless a different functional form can be satisfactorily justified to describe the distribution of the sntr value

s. Thus

    • sntr is the upper one-sided 95/95 tolerance limit for the density changes and can be obtained from the sample values using one of the methods outlined belo

w.

1 It is incorrect to prorate the characterizations of the contributing subsets by computing weighted averages over the subsets.

Rev. 2 of RG 1.126, Page 5 3.1.1 Normal Distribution In this case, **sntris given by the following:

    • sntr = sntr + c's, where sntr is the mean of the sample data, s is the standard deviation of the sample data, and c' is given in Table 1 (from Ref. 4).

Table 1 Values To Be Used for c' To Determine

    • sntr with Normal Distribution Number of Observationsc' 4 5.15 5 4.20 6 3.71 7 3.40 8 3.19 9 3.03 10 2.91 11 2.82 12 2.74 15 2.57 20 2.40 25 2.29 30 2.22 40 2.13 60 2.02 100 1.93 200 1.84 500 1.76 1.64 3.1.2 Nonnormal Distribution In this case, **sntris given by the following:
    • sntr = )(m sntr, where )(m sntr is the m th largest sntr value in a ranking of the observed values of sntr from the sample. The integer m depends on the sample size according to Table 2 (from Ref. 5).

This method requires a minimum of 60 observations to produce a meaningful result.

Rev. 2 of RG 1.126, Page 6 Table 2 Values To Be Used for m To Determine

    • sntr with Nonnormal Distribution Number of Observations m 50 - 55 - 60 1 65 1 70 1 75 1 80 1 85 1 90 1 95 2 100 2 110 2 120 2 130 3 140 3 150 3 170 4 200 5 300 9 400 13 500 17 600 21 700 26 800 30 900 35 1000 39 3.2 Multiple-Pellet Effects Average pellet behavior determines changes in fuel column length, which can result in axial gaps in the pellet stack. In this case, however, the population to be considered is not the core or reload quantity characterized above, but rather the material population (or subset thereof) within that quantity that exhibits the largest mean of the sntrvalues from the sample. The distribution of sntrvalues for the selected material population may be assumed to be normal.

To analyze effects related to column-length changes, resintering-based densification models should use a density change value

  • sntrthat bounds the selected material population mean with 95-percent confidence. Thus, *sntris the upper one-sided 95-percent confidence limit on the mean

Rev. 2 of RG 1.126, Page 7 density change and can be obtained from the sample values using the following expression:

  • sntr = sntr'+ cs', where sntr'is the mean of the sample data from the selected material population, s' is the standard deviation of the sample data from the selected material population, and c is given in Table 3 (from Ref. 4). Table 3 Values To Be Used for c To Determine
  • sntr Number of Observations c 4 1.18 5 0.95 6 0.82 7 0.73 8 0.67 9 0.62 10 0.58 11 0.55 12 0.52 15 0.45 20 0.39 25 0.34 30 0.31 40 0.27 60 0.22 100 0.17 200 0.12 500 0.07 0 4. Measurement Methods To measure the density change sntr during resintering, either geometric or true densities may be used, so long as the same method is used before and after resintering. Techniques such as vacuum impregnation/water immersion, mercury immersion, gamma-ray absorption, and mensuration are acceptable. It is also acceptable to infer the density change from a diameter change, using the isotropic relation /sntr = 3 D D sntr/, where sntr D is the diameter change experienced during resintering.

Resintering should be performed in a furnace with a known temperature distribution in the working region. Temperatures during resintering should be measured using either thermocouples or calibrated optical methods with established blackbody conditions. Furnace temperatures should be maintained so that specimen temperatures are no lower than the desired test temperature (1700 °C or 3092 °F for 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> in the model above) after temperature measurement errors have been taken into account.

Rev. 2 of RG 1.126, Page 8 In considering fuel stoichiometry, an oxygen-to-metal ratio of approximately 2.00 should be maintained. This may be accomplished by using dry tank hydrogen or dry gas mixtures (e.g., N

2-H 2) and avoiding temperatures in excess of about 1800 °C (3272 °F).

5. Isotropy Assumptions To use predicted density changes in a calculation of the effects of in-reactor densification, it is necessary to make some assumption about the isotropy of fuel densification. For changes in pellet diameter D, isotropic densification may be assumed, so that D/D = /3. For changes in pellet or fuel column length L, anisotropic densification is assumed such that L/L = /2. For further discussion of the conservative nature of these assumptions, see Section III. D of NUREG-008

5.

D. IMPLEMENTATION

The purpose of this section is to provide information to applicants and licensees regarding the NRC's plans for using this regulatory guide. The NRC does not intend or approve any imposition or backfit in connection with its issuance.

In some cases, applicants or licensees may propose or use a previously established acceptable alternative method for complying with specified portions of the NRC's regulations. Otherwise, the methods described in this guide will be used in evaluating compliance with the applicable regulations for license applications, license amendment applications, and amendment requests.

Rev. 2 of RG 1.126, Page 9 TERMS USED IN EQUATIONS

The following identifies the major symbols used in Section C:

BU burn up unit expressed in megawatt days per metric ton of heavy metal (MWd/t)

c, c' population parameters in Tables 1 and 3

D nominal initial pellet diameter, centimeters (cm)

L nominal fuel column length, cm m population parameter from Table 2

s standard deviation of the sample data s' standard deviation of the sample data from the selected material population

TD theoretical density, grams per cubic centimeter (g/cm

3) D in-reactor pellet diameter change (function of burnup), cm sntr D measured diameter change of a pellet resulting from ex-reactor resintering, cm L in-reactor fuel column length change (function of burnup), cm in-reactor pellet density change (function of burnup), g/cm

3 sntr measured density change of a pellet resulting from ex-reactor resintering, g/cm

3 sntr mean of the measured density change data, sntr, g/cm 3 sntr' mean of a selected material population of the measured density data, sntr, g/cm 3 *sntr one-sided 95-percent upper confidence limit on the mean of the sntr values from the selected material population, g/cm

3 **sntr one-sided 95/95 upper tolerance limit for the total population of sntrvalues, g/cm

3 nominal initial pellet density, g/cm

3 Rev. 2 of RG 1.126, Page 10

REFERENCES

1 1. 10 CFR Part 50, "Domestic Licensing of Production and Utilization Facilities," U.S. Nuclear Regulatory Commission, Washington, DC.

2. NUREG-0085, "The Analysis of Fuel Densification," R.0. Meyer, U.S. Nuclear Regulatory Commission, Washington, DC, July 1976.

3. ANSI Standard N15.15-1974, "Assessment of the Assumption of Normality (Employing Individual Observed Values)," American National Standards Institute.

2 4. G.J. Hahn, "Statistical Intervals for a Normal Population, Part I. Tables, Examples and Applications," J. Quality Technol. 2, 115, 1970.

5. P.N. Somerville, "Tables for Obtaining Non-Parametric Tolerance Limits," Ann. Math. Stat. 29, pp. 599-601, 1958.

1 Publicly available NRC published documents such as Regulations, Regulatory Guides, NUREGs, and Generic Letters listed herein are available electronically through the Electronic Reading Room on the NRC's public Web site at:

http://www.nrc.gov/reading-rm/doc-collections/. Copies are also available for inspection or copying for a fee from the NRC's Public Document Room (PDR) at 11555 Rockville Pike, Rockville, MD; the mailing address is USNRC PDR, Washington, DC 20555; telephone 301-415-4737 or (800) 397-4209; fax (301) 415-3548; and e-mail

PDR.Resource@nrc.gov. 2 Copies of the non-NRC documents included in these references may be obtained directly from the publishing organization.