Author(s): Mei Ding, Amr Abdel-Fattah, Stewart Fischer,

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LA-UR-04-3970Approved for public release;distribution is unlimited.Title:Author(s):Characterization and Head-Loss Testing of LatentDebris from Pressurized-Water-Reactor ContainmentBuildingsMei Ding, Amr Abdel-Fattah, Stewart Fischer,and Bruce LetellierLos Alamos National LaboratoryKerry Howe and Janet GarciaUniversity of New MexicoClint ShafferAres Corporation, Albuquerque, NMSubmitted to:United States Nuclear Regulatory CommissionLos Alamos National Laboratory, an affirmative action/equal opportunity employer, is operated by the University of California for the U.S.Department of Energy under contract W-7405-ENG-36. By acceptance of this article, the publisher recognizes that the U.S. Governmentretains a nonexclusive, royalty-free license to publish or reproduce the published form of this contribution, or to allow others to do so, for U.S.Government purposes. Los Alamos National Laboratory requests that the publisher identify this article as work performed under theauspices of the U.S. Department of Energy. Los Alamos National Laboratory strongly supports academic freedom and a researcher’s right topublish; as an institution, however, the Laboratory does not endorse the viewpoint of a publication or guarantee its technical correctness.Form 836 (8/00)

LA-UR-04-3970Characterization and Head-Loss Testing ofLatent Debris from Pressurized-Water-ReactorContainment BuildingsManuscript Completed: August 2004Date Published: August 2004Principal Investigator: B. C. LetellierPrepared byMei Ding, Amr Abdel-Fattah, Stewart Fischer, Bruce Letellier, Kerry Howe,* Janet Garcia,* and ClintShaffer†Los Alamos National LaboratoryLos Alamos, NM 87545*The University of New MexicoDepartment of Civil EngineeringAlbuquerque, NM 87110†ARES CorporationAlbuquerque, NM 87106Tsun-Yung Chang, NRC Project ManagerPrepared for theDivision of Engineering TechnologyOffice of Nuclear Regulatory ResearchUS Nuclear Regulatory CommissionWashington, D.C. 20555-0001ii

LA-UR-04-3970EXECUTIVE SUMMARYThe study documented in this report does not represent a new issue; rather, the subject of latent debris hasbeen discussed in several public meetings before, and the preliminary test results of this study werepresented by Los Alamos National Laboratory (LANL) in the Nuclear Energy Agency/NuclearRegulatory Commission (NEA/NRC) international workshop on “Debris Impact on Emergency CoolantRecirculation” in February 2004. In addition, this subject was discussed during the Advisory Committee,Reactor Safeguards (ACRS) Thermal-Hydraulics Subcommittee meeting on June 23, 2004, and is alsobeing addressed in the Nuclear Energy Institute (NEI) industry guidance document “PWR ContainmentSump Evaluation Methodology (Draft, May 2004).”When accounting for the total amount of debris that may be present in a pressurized-water-reactor (PWR)containment pool during operation of the Emergency Core-Cooling System (ECCS), it is important toinclude a reasonable estimate of the amount of dirt, fiber, and foreign material that can be found incontainment, in addition to the debris generated by a loss-of-coolant accident (LOCA). Dirt and fiber thatnormally reside in containment are referred to herein as latent debris. Past and recent testing has shownthat even small quantities of fibrous debris that are present on an ECCS sump screen can filter particulatesthat are present in the sump pool, thereby leading to increased pressure losses across the composite debrisbed. Latent debris that is subjected to containment spray and pool transport may contribute an additionalsource of particulate and fiber material, or in some cases, it may represent the only significant source offiber that is available to form and retain a debris bed on the sump screen.Both the physical characteristics and the total inventory of latent debris must be understood to assess thepotential contribution of this material to recirculation-flow head loss. This report does not provideestimates of total containment inventory, which can vary depending on plant geometry and plantcleanliness practices. However, LANL, under the direction of the United States Nuclear RegulatoryCommission, has worked to characterize the material composition and hydraulic flow properties of actualplant debris samples. Beginning in August 2003 and ending in June 2004, this study has attempted toquantify latent-debris parameters—such as the fiber-to-particulate mass ratio, particulate sizedistributions, and the hydraulic properties of specific surface area (SSA) and porosity—that are neededfor the proper application of the NUREG/CR 62241 head-loss correlation. Sieving, optical microscopy,scanning electron microscopy, energy-dispersive spectroscopy, and nitrogen adsorption tests were used tofractionate and characterize the fibrous and particulate components. These tests were performed in thegeochemistry laboratory of the Isotope and Nuclear Chemistry Facility at LANL, which has the necessaryanalytic equipment and safety procedures to handle and dispose of small quantities of low-levelradioactive debris. Five volunteer PWR plants contributed latent-debris samples, which were collectedduring their recent condition assessment surveys.Hydraulic parameters representative of latent particulates were measured by testing larger quantities ofsurrogate debris in a vertical-flow test loop at the University of New Mexico (UNM). This apparatuspermits measurement of pressure drop (head loss) across a debris bed of known composition under arange of water velocities. Hydraulic parameters can be inferred from differential pressure data byiteratively applying predictive correlations until the model results envelop a variety of observed behavior.Surrogate particulate debris was generated by dry-sieving soil and sand into a range of particle diametersusing different sieve sizes and by recombining mass fractions to match the size distribution measured inthe plant samples. The microflow characteristics of the surrogate also were compared to those of the plantdebris by measuring packed-bed flow conductivity.1G. Zigler, J. Brideau, D. V. Rao, C. Shaffer, F. Souto, and W. Thomas, “Parametric Study of the Potential for BWR ECCSStrainer Blockage Due to LOCA Generated Debris,” United States Nuclear Regulatory Commission final report NUREG/CR6224, Science and Engineering Associates, Inc., report SEA-93-554-06-A:1 (October 1995).iii

LA-UR-04-3970The hydraulic parameters of latent fiber are assumed to be the same as those for fiberglass insulation.Fiber surrogates were not investigated in detail because the head-loss contribution of latent fiber eitherwill be dominated by particulates in thin-bed configuration or will represent a small increase to afiberglass-dominated debris composition. Further, the characterization of latent fiber samples led LANLto conclude that it is conservative to assume that the latent fiber component has similar hydraulicproperties to those of fiberglass. For these reasons, fiberglass is used as surrogate for latent fibers and thelatent fiber fraction was not isolated for hydraulic testing in this study.Foreign material (or the “other” debris category) was deemed unnecessary to be part of the surrogatedebris. This foreign material consists of larger material, such as bolts, nuts, cable ties, and rags, and is notexpected to be transported to the cooling system screen under recirculation flow velocities or to contributeto the formation of a uniform debris bed on the screen. The full range of sizes of latent debris, includingthis foreign material, should be considered if it is subject to high-velocity water transport toward theECCS screen, such as during the high-velocity sump-pool fill.The principal findings of this study are based on analyses of samples from the volunteer PWRs. Sampleswere collected during refueling outages, sometimes before restart cleanliness procedures and sometimesafter. All analyses are based on the assumption that proportional debris compositions are approximatelyconstant even if the total inventory varies during an outage or during a plant lifetime. These samplesrepresent the best information to date regarding latent containment debris but may not capture the fullrange of variability present in the population of nuclear power plants. Furthermore, the quality of thedebris samples varied widely because of differences in collection methods and sample locations.Recommendations made in Section 5, “Conclusions and Recommendations,” are intended to providegeneral guidance for plant-specific assessment of latent-debris contributions to sump-screen head loss.However, because of the limitation of data collected for this study, these recommendations may not beapplicable to some of the operating PWR plants. In these cases, plant-specific debris characterization maybe preferable to the default properties recommended.iv

LA-UR-04-3970ACKNOWLEDGMENTSThis project could not have been accomplished without the coordination efforts of the Nuclear EnergyInstitute and the cooperation of the five member utilities who submitted samples and freely discussedtheir individual debris-collection strategies. Their participation has improved the knowledge base relevantto potential sump-screen blockage and has provided insights that will benefit the entire nuclear utilitycommunity. Lab assistants William Roesch and James Madrid of LANL’s Nuclear Design & RiskAnalysis Group (D-5) and Doug Ware of LANL’s Isotope and Nuclear Chemistry Group (C-INC) arerecognized for their dedicated attention to detail during the hydraulic test procedures. Paul Reimus, alsoof LANL’s C-INC Group, is appreciated for providing access to the radionuclide geochemistry lab forthis rather unusual project. The authors would also like to express their gratitude for the contributions ofTsun-Yung Chang, Tony Hsia, and other NRC staff members who reviewed the final report to improve itsclarity, and quality.v

ller (Method)Barrett/Joyner/Halenda (Method)Boiling-Water ReactorCode of Federal RegulationsDesign GuideEmergency Core-CoolingEmergency Core-Cooling SystemEnergy-Dispersive SpectroscopyHigh-Efficiency Particulate AirHorvath/Kawazoc (Method)Los Alamos National LaboratoryLoss-of-Coolant AccidentNephelometric Turbidity UnitsPolyvinyl ChloridePressurized-Water ReactorScanning Electron MicroscopeSpecific Surface AreaUniversity of New MexicoUnited States Nuclear Regulatory Commissionvi

LA-UR-04-3970CONTENTSPageEXECUTIVE SUMMARY . iiiACKNOWLEDGMENTS .viACRONYMS .viiFIGURES.ixTABLES.xi1.0 INTRODUCTION.12.0 BACKGROUND AND PURPOSE.13.0 PHYSICAL CHARACTERIZATION OF LATENT-DEBRIS SAMPLES.33.1 Experimental Protocol.33.1.1 Removal of Debris from Shipping Containers.43.1.2 Separation of “Fiber” and “Particle” with Sieving .43.1.3 Weight of Fine Particles Attached to Cloth and Filter Paper.163.1.4 Determination of Fiber Thickness/Diameter .193.1.5 Estimation of Material and Filter-Bed Fiber Density .193.1.6 BET Surface Area and Density Measurement of Particles.233.1.7 Microphotographic Classification of Fibers .233.1.8 Scanning Electron Microscope/Energy-Dispersive Spectroscopy.233.2 Characterization Results and Discussion .253.2.1 Composition of Debris.253.2.2 Classification of Fibers .353.2.3 Fiber Density and Thickness/Diameter Measurements .373.2.4 BET Surface Area and Density of Particles in Latent Debris.403.2.5 Characteristics of Pores in Latent Debris.423.3 Guidance for Preparation of Surrogate Debris .444.0 HYDRAULIC MEASUREMENT OF SURROGATE DEBRIS .454.1 Surrogate Debris Formula .454.1.1 “Other” and Fiber Surrogate Debris Fractions.454.1.2 Particulate Surrogate Debris Fraction.464.2 Microflow Comparisons.484.3 Surrogate Debris Head-Loss Testing .535.0 CONCLUSIONS AND RECOMMENDATIONS.65APPENDIX A: SURROGATE LATENT-PARTICULATE HEAD-LOSS TESTS .72vii

LA-UR-04-3970FIGURESPageFig. 1. Representative latent plant debris as shipped. . 5Fig. 2. Composition of debris (Plant A). 6Fig. 3. Fiber (Plant A). . 6Fig. 4. Fiber (Plant B). . 7Fig. 5. Particulate 2 mm (Plant A). . 7Fig. 6. Particulate 500 µm to 2 mm (Plant A). 8Fig. 7. Particulate 75 µm to 500 µm (Plant A). 8Fig. 8. Particulate 75 µm (Plant A). 9Fig. 9. Particulate 2 mm (Plant B). . 9Fig. 10. Particulate 500 µm to 2 mm (Plant B). . 10Fig. 11. Particulate 75 µm to 500 µm (Plant B). 10Fig. 12. Particulate 75 µm (Plant B). . 11Fig. 13. Fiber (Plant C). . 11Fig. 14. Fiber (Plant D). . 12Fig. 15. Particulate 2 mm (Plant C). . 12Fig. 16. Particulate 500 µm to 2 mm (Plant C). . 13Fig. 17. Particulate 75 µm to 500 µm (Plant C). 13Fig. 18. Particulate 75 µm (Plant C). . 14Fig. 19. Particulate 2 mm (Plant D). . 14Fig. 20. Particulate 500 µm to 2 mm (Plant D). 15Fig. 21. Particulate 75 µm to 500 µm (Plant D). 15Fig. 22. Particulate 75 µm (Plant D). 16Fig. 23. Qualitative flow schematic for separation of latent debris. . 17Fig. 24. Clean masolin cloth (Plant D). 17Fig. 25. Dirty masolin cloth (Plant D). . 18Fig. 26. Photo images of fiber (Plant A). . 20Fig. 27. Photo images of fiber (Plant B). . 21Fig. 28. Photo images of fiber (Plant C). . 22Fig. 29. Nitrogen adsorption BET instrumentation. 24Fig. 30. Metallurgical microscope. . 24Fig. 31. SEM/EDS instrumentation. . 25Fig. 32. SEM image of Plant-A fibers at 100 µm. . 28Fig. 33. SEM image of Plant-A fibers at 10 µm. . 28Fig. 34. Composition of latent debris from Plants A, B, and C. . 30Fig. 35. Weight fraction of particles and fibers for Plants A, B, C, and D. . 31Fig. 36. SEM photo of 75- to 500-µm particles from Plant A. . 33Fig. 37. SEM photo of fines 75 µm from Plant B. 33Fig. 38. X-ray analysis of 75- to 500-µm particles from Plant A. . 34Fig. 39. Particle-size distributions of latent debris of Plants A, B, and D. . 36Fig. 40. Distribution of measured fiber thickness/diameter for Plants A, B, and C. 37Fig. 41. Collective thickness/diameter distribution. 38Fig. 42. SSA and density of latent debris as a function of its particle size. . 41Fig. 43. SSA and density of latent debris as a function of particle size.

Mei Ding, Amr Abdel-Fattah, Stewart Fischer, Bruce Letellier, Kerry Howe,* Janet Garcia,* and Clint Shaffer† Los Alamos National Laboratory Los Alamos, NM 87545 *The University of New Mexico Department of Civil Engineering Albuquerque, NM 87110 †ARES Corporation Albuquerque, NM 87

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