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Sandia National Laboratories is a multi-program laboratory managed and operated by Sandia
Corporation, a wholly owned subsidiary of Lockheed Martin Corporation, for the U.S. Department
of Energy’s National Nuclear Security Administration under contract DE-AC04-94AL85000. This
research is funded by WIPP programs administered by the Office of Environmental Management
(EM) of the U.S. Department of Energy.
SAND2016-8665C.
Parameter Selections Associated with Modeling
WIPP’s ROM Salt Panel Closure System
Courtney G Herrick
Sandia National Laboratories
Washington, DC
September 7-9, 2016
Outline
 WIPP background, panel closure history
 Option D
 Panel closure design elements
 WIPP ROM (Run-of-Mine) Salt Panel Closure System
 Construction attempts at ROM Salt Panel Closures
 Three scenarios
 Parameters and their evaluation to use the “WIPP
Crushed Salt Model” (Callahan, 1999)
 Geometry
 Initial density
 Moisture content
 Particle size
2
WIPP Background
 Deep Geologic Repository in
Bedded Salt
 Disposal of U.S. defense
related Transuranic and
Transuranic Mixed waste
 Repository Design consists of:
 Ten panels
 Each panel has seven rooms
 Two access drifts per panel
 Intake
 Exhaust
 Five Options for Panel
Closures were submitted.
Option D was chosen by the
EPA
3
Option D Panel Closure
 1998: EPA’s Certification decision identified Option D with Salado
Mass Concrete (salt-based concrete) as the mandated panel closure
design. Long-term repository performance 10,000 yrs.
 1999: NMED agreed with EPA’s mandated design and incorporated
Option D with Salado Mass Concrete into the Hazardous Waste
Facility Permit. Short-term repository performance ≈30 yrs.
4
Problems with Options D
DOE identified issues with construction of Option D:
 Cannot manufacture Salado mass concrete to the
specifications in the compliance application while
meeting the design requirements of the Option D design
 Option D design is very complex to implement and
impacts waste handling operations
 Hydrogen and Methane monitoring data shows no need
for explosion wall
5
Panel Closure Redesign
Criteria
 The panel closure system design shall limit VOC migration
from a closed panel consistent with the limits found in the
Hazardous Waste Permit
 The panel closure system shall consider potential flow of
VOCs through the disturbed rock zone (DRZ) in addition to
flow through the closure components
 The panel closure system shall perform its intended functions
under loads generated by creep closure of the drifts
 The nominal operational life of the closure system is thirty-five
(35) years
 The panel closure system shall address the most severe
ground conditions expected in the waste disposal area
 The panel closure system shall be built to generally accepted
national design and construction standards
6
Redesign Criteria Cont.
 The design and construction shall follow conventional mining
practices
 Structural analysis shall use data acquired from the WIPP
underground
 Materials shall be compatible with the emplacement
environment and function
 Treatment of surfaces in the closure areas shall be
considered in the design
 During construction, a Quality Assurance/Quality Control
(QA/QC) program shall be established to verify material
properties and construction practices
 Construction of the panel closure system shall consider shaft
and underground access and services for materials handling
7
The Original WIPP Panel
Closure (WPC) Design
8
Nuclear Waste Partnership’s
(NWP) Construction Attempts
Modified from Klein, T., Patterson, R., Camphouse, C., et al. (2013.) In-Situ Testing and Performance Assessment of a Redesigned
WIPP Panel Closure. Paper 13192. WM2013 Conference, 24-28 Feb 2013, Phoenix, Arizona.
9
Construction Techniques
10
Load-Haul-Dump
Truck Placing
ROM Salt
Walk Behind
Roller Compactor
Fletcher with
Push-Plate
Attachment
Numerical Modeling
 Our numerical modeling intention was always to use
the “WIPP Crushed Salt Model” developed by Gary
Callahan
Callahan, G.D. (1999.) Crushed Salt Constitutive
Model. SAND98-2680. Sandia National Laboratories,
Albuquerque, New Mexico.
 The model is dependent on:
 Grain size
 Moisture content
 Temperature
11
Scenario Summaries (Averages)
It was decided that the addition of 1% moisture by weight (Scenario 1)
and performing initial compaction to 75% (Scenarios 1 and 2) resulted
in fractional densities that were only 10% greater than the simpler ROM
salt emplacement of Scenario 3 and does not support the cost of the
increased effort involved.
12
Scenario 1 Scenario 2 Scenario 3
Lower Level Compaction
(% Intact Salt Density)
74.5 74.4 –
Lower Level Moisture Content (%) 1.57 0.31 –
Upper Level Compaction
(% Intact Salt Density)
63.2 62.5 66.8
Upper Level Moisture Content (%) 1.30 0.40 0.43
Zimmerly, B., Moffat, T., and Zavicar IV, J. (2012.) Construction Methods Assessment for Compacted Salt Panel Closure.
Nuclear Waste Partnership LLC, Carlsbad, New Mexico
Final WPC Design
13
2
1
2
1
100'-0"
Bulkhead Bulkhead
2
1
100'-0"
Bulkhead
Existing
Explosion
Wall
Waste
Disposal
Side
Waste
Disposal
Side
Modified from Klein, T., Patterson, R., Camphouse, C., et al. (2013.) In-Situ Testing and Performance Assessment of a
Redesigned WIPP Panel Closure. Paper 13192. WM2013 Conference, 24-28 Feb 2013, Phoenix, Arizona.
Character of ROM Salt
 Large Range of Sizes – Boulders to Silt
14
Prototype Panel Closure ROM
Salt Sieve Analysis
15
ROM Grain Size Distribution
SA-1
16
Material used for Proctor tests; boulders greater than 3 inch in
diameter discarded prior to test
ROM Grain Size Distribution
SA-2
17
Material used for Proctor tests; boulders greater than 3 inch in
diameter discarded prior to test
ROM Grain Size Distribution
SA-3
18
Material used for Proctor tests; boulders greater than 3 inch in
diameter discarded prior to test
ROM Grain Size Distribution
SA-4
19
Material used for panel closure demonstration (Slide 15). Distribution
of boulders greater than 3 inch in diameter not analyzed (9% of total)
Comments on Grain Sizes
Analyses
 This ROM salt grain size distributions are not normal or
theoretically expected lognormal curves under grinding and
crushing, but are generally polymodal
 Sedimentologists have developed a number of graphic and
moment measures to determine grain size statistics
 The WIPP ROM salt data is already skewed because most
labs, apparently including the lab which performed the
gradation tests for NWP, cannot accommodate the boulders
found in the material
 Large sieves
 Large sample (6 inch sieve  recommended minimum sample size of
1,250 lbs / 575 kg) (extrapolated from ASTM D6913-04, Table 2)
20
Inclusive Graphics
21
Poppe, L.J., McMullen, K.Y., Williams, S.J., and
Paskevich, V.F., eds. (2014.) USGS east-coast
sediment analysis: Procedures, database, and
GIS data, U.S. Geological Survey Open-File
Report 2005-1001, available online at
http://pubs.usgs.gov/of/2005/1001/
Method of Moments
22
Poppe, L.J., McMullen, K.Y.,
Williams, S.J., and Paskevich, V.F.,
eds. (2014.) USGS east-coast
sediment analysis: Procedures,
database, and GIS data, U.S.
Geological Survey Open-File Report
2005-1001, available online at
http://pubs.usgs.gov/of/2005/1001/
Estimates of Mean Particle Size
 Calculations performed using GRADISTAT v.8 (Kenneth Pye
Assoc.)
 Method of Moments statistics compares well with GSSTAT (USGS,
Woods Hole Coastal and Marine Science Center)
 Inclusive Graphics statistics verified by hand-calculations
23
Median
(μm / ϕ)
Incl. Graph. Mean
(μm / ϕ)
Meth. of Mom. Mean
(μm / ϕ)
SA-1 4233.1 / -2.082 4641.4 / -2.215 4070.5 / -2.025
SA-2 8004.2 / -3.001 8410.3 / -3.072 7269.9 / -2.862
SA-3 2784.7 / -1.478 2335.3 / -1.224 2178.7 / -1.123
SA-4 4356.0 / -2.123 5164.2 / -2.369 4122.8 / -2.044
Recommended value
Poorly sorted, sandy very coarse gravel
Blott, S.L. and Pye, K. (2001.) GRADISTAT: A Grain Size Distribution and Statistics Package for the Analysis of Unconsolidated
Sediments. Earth Surf. Process. Landforms 26: 1237–1248.
Conclusion
 Needed input parameters for mean grain size, moisture content,
initial density, and geometry to use the “WIPP Crushed Salt Model”
(Callahan, 1999) to model the WPC
 Parameters and model geometries were obtained from NWP’s three
panel closure construction demonstrations
24
WM2013 Presentation for Klein, T., Patterson, R., Camphouse, C., et al. (2013.) In-Situ Testing and Performance Assessment of
a Redesigned WIPP Panel Closure. Paper 13192. WM2013 Conference, 24-28 Feb 2013, Phoenix, Arizona.
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21 herrick parameter selections sand2016 8665 c

  • 1. Sandia National Laboratories is a multi-program laboratory managed and operated by Sandia Corporation, a wholly owned subsidiary of Lockheed Martin Corporation, for the U.S. Department of Energy’s National Nuclear Security Administration under contract DE-AC04-94AL85000. This research is funded by WIPP programs administered by the Office of Environmental Management (EM) of the U.S. Department of Energy. SAND2016-8665C. Parameter Selections Associated with Modeling WIPP’s ROM Salt Panel Closure System Courtney G Herrick Sandia National Laboratories Washington, DC September 7-9, 2016
  • 2. Outline  WIPP background, panel closure history  Option D  Panel closure design elements  WIPP ROM (Run-of-Mine) Salt Panel Closure System  Construction attempts at ROM Salt Panel Closures  Three scenarios  Parameters and their evaluation to use the “WIPP Crushed Salt Model” (Callahan, 1999)  Geometry  Initial density  Moisture content  Particle size 2
  • 3. WIPP Background  Deep Geologic Repository in Bedded Salt  Disposal of U.S. defense related Transuranic and Transuranic Mixed waste  Repository Design consists of:  Ten panels  Each panel has seven rooms  Two access drifts per panel  Intake  Exhaust  Five Options for Panel Closures were submitted. Option D was chosen by the EPA 3
  • 4. Option D Panel Closure  1998: EPA’s Certification decision identified Option D with Salado Mass Concrete (salt-based concrete) as the mandated panel closure design. Long-term repository performance 10,000 yrs.  1999: NMED agreed with EPA’s mandated design and incorporated Option D with Salado Mass Concrete into the Hazardous Waste Facility Permit. Short-term repository performance ≈30 yrs. 4
  • 5. Problems with Options D DOE identified issues with construction of Option D:  Cannot manufacture Salado mass concrete to the specifications in the compliance application while meeting the design requirements of the Option D design  Option D design is very complex to implement and impacts waste handling operations  Hydrogen and Methane monitoring data shows no need for explosion wall 5
  • 6. Panel Closure Redesign Criteria  The panel closure system design shall limit VOC migration from a closed panel consistent with the limits found in the Hazardous Waste Permit  The panel closure system shall consider potential flow of VOCs through the disturbed rock zone (DRZ) in addition to flow through the closure components  The panel closure system shall perform its intended functions under loads generated by creep closure of the drifts  The nominal operational life of the closure system is thirty-five (35) years  The panel closure system shall address the most severe ground conditions expected in the waste disposal area  The panel closure system shall be built to generally accepted national design and construction standards 6
  • 7. Redesign Criteria Cont.  The design and construction shall follow conventional mining practices  Structural analysis shall use data acquired from the WIPP underground  Materials shall be compatible with the emplacement environment and function  Treatment of surfaces in the closure areas shall be considered in the design  During construction, a Quality Assurance/Quality Control (QA/QC) program shall be established to verify material properties and construction practices  Construction of the panel closure system shall consider shaft and underground access and services for materials handling 7
  • 8. The Original WIPP Panel Closure (WPC) Design 8
  • 9. Nuclear Waste Partnership’s (NWP) Construction Attempts Modified from Klein, T., Patterson, R., Camphouse, C., et al. (2013.) In-Situ Testing and Performance Assessment of a Redesigned WIPP Panel Closure. Paper 13192. WM2013 Conference, 24-28 Feb 2013, Phoenix, Arizona. 9
  • 10. Construction Techniques 10 Load-Haul-Dump Truck Placing ROM Salt Walk Behind Roller Compactor Fletcher with Push-Plate Attachment
  • 11. Numerical Modeling  Our numerical modeling intention was always to use the “WIPP Crushed Salt Model” developed by Gary Callahan Callahan, G.D. (1999.) Crushed Salt Constitutive Model. SAND98-2680. Sandia National Laboratories, Albuquerque, New Mexico.  The model is dependent on:  Grain size  Moisture content  Temperature 11
  • 12. Scenario Summaries (Averages) It was decided that the addition of 1% moisture by weight (Scenario 1) and performing initial compaction to 75% (Scenarios 1 and 2) resulted in fractional densities that were only 10% greater than the simpler ROM salt emplacement of Scenario 3 and does not support the cost of the increased effort involved. 12 Scenario 1 Scenario 2 Scenario 3 Lower Level Compaction (% Intact Salt Density) 74.5 74.4 – Lower Level Moisture Content (%) 1.57 0.31 – Upper Level Compaction (% Intact Salt Density) 63.2 62.5 66.8 Upper Level Moisture Content (%) 1.30 0.40 0.43 Zimmerly, B., Moffat, T., and Zavicar IV, J. (2012.) Construction Methods Assessment for Compacted Salt Panel Closure. Nuclear Waste Partnership LLC, Carlsbad, New Mexico
  • 13. Final WPC Design 13 2 1 2 1 100'-0" Bulkhead Bulkhead 2 1 100'-0" Bulkhead Existing Explosion Wall Waste Disposal Side Waste Disposal Side Modified from Klein, T., Patterson, R., Camphouse, C., et al. (2013.) In-Situ Testing and Performance Assessment of a Redesigned WIPP Panel Closure. Paper 13192. WM2013 Conference, 24-28 Feb 2013, Phoenix, Arizona.
  • 14. Character of ROM Salt  Large Range of Sizes – Boulders to Silt 14
  • 15. Prototype Panel Closure ROM Salt Sieve Analysis 15
  • 16. ROM Grain Size Distribution SA-1 16 Material used for Proctor tests; boulders greater than 3 inch in diameter discarded prior to test
  • 17. ROM Grain Size Distribution SA-2 17 Material used for Proctor tests; boulders greater than 3 inch in diameter discarded prior to test
  • 18. ROM Grain Size Distribution SA-3 18 Material used for Proctor tests; boulders greater than 3 inch in diameter discarded prior to test
  • 19. ROM Grain Size Distribution SA-4 19 Material used for panel closure demonstration (Slide 15). Distribution of boulders greater than 3 inch in diameter not analyzed (9% of total)
  • 20. Comments on Grain Sizes Analyses  This ROM salt grain size distributions are not normal or theoretically expected lognormal curves under grinding and crushing, but are generally polymodal  Sedimentologists have developed a number of graphic and moment measures to determine grain size statistics  The WIPP ROM salt data is already skewed because most labs, apparently including the lab which performed the gradation tests for NWP, cannot accommodate the boulders found in the material  Large sieves  Large sample (6 inch sieve  recommended minimum sample size of 1,250 lbs / 575 kg) (extrapolated from ASTM D6913-04, Table 2) 20
  • 21. Inclusive Graphics 21 Poppe, L.J., McMullen, K.Y., Williams, S.J., and Paskevich, V.F., eds. (2014.) USGS east-coast sediment analysis: Procedures, database, and GIS data, U.S. Geological Survey Open-File Report 2005-1001, available online at http://pubs.usgs.gov/of/2005/1001/
  • 22. Method of Moments 22 Poppe, L.J., McMullen, K.Y., Williams, S.J., and Paskevich, V.F., eds. (2014.) USGS east-coast sediment analysis: Procedures, database, and GIS data, U.S. Geological Survey Open-File Report 2005-1001, available online at http://pubs.usgs.gov/of/2005/1001/
  • 23. Estimates of Mean Particle Size  Calculations performed using GRADISTAT v.8 (Kenneth Pye Assoc.)  Method of Moments statistics compares well with GSSTAT (USGS, Woods Hole Coastal and Marine Science Center)  Inclusive Graphics statistics verified by hand-calculations 23 Median (μm / ϕ) Incl. Graph. Mean (μm / ϕ) Meth. of Mom. Mean (μm / ϕ) SA-1 4233.1 / -2.082 4641.4 / -2.215 4070.5 / -2.025 SA-2 8004.2 / -3.001 8410.3 / -3.072 7269.9 / -2.862 SA-3 2784.7 / -1.478 2335.3 / -1.224 2178.7 / -1.123 SA-4 4356.0 / -2.123 5164.2 / -2.369 4122.8 / -2.044 Recommended value Poorly sorted, sandy very coarse gravel Blott, S.L. and Pye, K. (2001.) GRADISTAT: A Grain Size Distribution and Statistics Package for the Analysis of Unconsolidated Sediments. Earth Surf. Process. Landforms 26: 1237–1248.
  • 24. Conclusion  Needed input parameters for mean grain size, moisture content, initial density, and geometry to use the “WIPP Crushed Salt Model” (Callahan, 1999) to model the WPC  Parameters and model geometries were obtained from NWP’s three panel closure construction demonstrations 24 WM2013 Presentation for Klein, T., Patterson, R., Camphouse, C., et al. (2013.) In-Situ Testing and Performance Assessment of a Redesigned WIPP Panel Closure. Paper 13192. WM2013 Conference, 24-28 Feb 2013, Phoenix, Arizona.
  • 25. Sorry, no results yet. Dinner is still in the oven. 25