RPP-RPT-50703 Rev.01A 8/23/2016 - 10:10 AM 1 of 77
Release Stamp DOCUMENT RELEASE AND CHANGE FORM
Prepared For the U.S. Department of Energy, Assistant Secretary for Environmental Management By Washington River Protection Solutions, LLC., PO Box 850, Richland, WA 99352 Contractor For U.S. Department of Energy, Office of River Protection, under Contract DE-AC27-08RV14800 DATE: TRADEMARK DISCLAIMER: Reference herein to any specific commercial product, process, or service by trade name, trademark, manufacturer, or otherwise, does not necessarily constitute or imply its endorsement, recommendation, or favoring by the United States government or any agency thereof or its contractors or subcontractors. Printed in the United States of America. Aug 23, 2016 1. Doc No: RPP-RPT-50703 Rev. 01A
2. Title: Development of a Thermodynamic Model for the Hanford Tank Waste Simulator (HTWOS) 3. Project Number: ☒ N/A 4. Design Verification Required: ☐ Yes ☒ No 5. USQ Number: ☒ N/A 6. PrHA Number Rev. ☒ N/A Clearance Review Restriction Type: public
7. Approvals Title Name Signature Date Checker CREE, LAURA H CREE, LAURA H 08/16/2016 Clearance Review RAYMER, JULIA R RAYMER, JULIA R 08/23/2016 Document Control Approval MANOR, TAMI MANOR, TAMI 08/23/2016 Originator BRITTON, MICHAEL D BRITTON, MICHAEL D 08/16/2016 Quality Assurance DELEON, SOSTEN O DELEON, SOSTEN O 08/16/2016 Responsible Manager CREE, LAURA H CREE, LAURA H 08/16/2016 8. Description of Change and Justification Updated the reduced chemical potential coefficient vlaues for Na2SO4 and Na2SO4·10H2O in Table A.1, as the original values were incorrect. Added mineral names for double salts NaNO2·Na2SO4·H2O, Na3FSO4, and Na7F(PO4)2·19H2O for consistency with other double sales evaluated. Changed the name of the author's company from EnergySolutions to Atkins Global on the cover page.
9. TBDs or Holds ☒ N/A
10. Related Structures, Systems, and Components a. Related Building/Facilities ☒ N/A b. Related Systems ☒ N/A c. Related Equipment ID Nos. (EIN) ☒ N/A
11. Impacted Documents – Engineering ☒ N/A Document Number Rev. Title
12. Impacted Documents (Outside SPF): N/A 13. Related Documents ☐ N/A Document Number Rev. Title RPP-51192 00 Plan for Evaluation of the HTWOS Integrated Solubility Model Predictions RPP-PLAN-46002 00 WASH AND LEACH FACTOR WORK PLAN SVF-2375 00 SVF-2375-Rev0_GEMS.xlsm 14. Distribution Name Organization ARM, STUART T ONE SYS RPP INTEGRTD FLOWSHEET BELSHER, JEREMY D ONE SYS SYSTEM PLNG & MODELING BERGMANN, LINDA M ONE SYS SYSTEM PLNG & MODELING BRITTON, MICHAEL D ONE SYS PROJECT FLOWSHEETS HERTING, DANIEL L PROCESS CHEMISTRY HO, QUYNH-DAO T ONE SYS PROJECT FLOWSHEETS JASPER, RUSSELL T ONE SYS SYSTEM PLNG & MODELING REAKSECKER, SEAN D ONE SYS SYSTEM PLNG & MODELING REYNOLDS, JACOB G TNK WST INVENTORY & CHARACTZTN
1 SPF-001 (Rev.D1) RPP-RPT-50703 Rev.01A 8/23/2016 - 10:10 AM 2 of 77
RPP-RPT-50703, Rev. 1A
Development of a Thermodynamic Model for the Hanford Tank Waste Simulator (HTWOS)
R. Carter Atkins Global, LLC 2345 Stevens Drive, Suite 240 Richland, WA 99352 U.S. Department of Energy Contract DE-AC27-08RV14800
EDT/ECN: DRF UC: Cost Center: 2PH00 Charge Code: B&R Code: Total Pages: 77 TM 08/23/16 Key Words: Thermodynamics, Pitzer ion interaction model, water activity, solute activity, molality, ionic strength, solubility, Hanford crystal phases, osmotic coefficient, activity coefficient, HTWOS.
Abstract: This report describes the multicomponent Pitzer ion interaction model and the development of a database of temperature dependent parameter coefficients for ultimate use with the model in the Hanford Tank Waste Simulator (HTWOS). The bulk components included in the termodynamic model include sodium nitrate, sodium nitrite, sodium hydroxide, sodium fluoride, sodium chloride, sodium carbonate, sodium phosphate, sodium oxalate and gibbsite. To ensure the final parameters were self-consistent, they were optimized by fitting the model to experimentally determined solubility data.This optimized model allows predictions of phase speciation to high ionic strengths and temperatures from 0 to 100 °C for Hanford Tank waste.
TRADEMARK DISCLAIMER. Reference herein to any specific commercial product, process, or service by trade name, trademark, manufacturer, or otherwise, does not necessarily constitute or imply its endorsement, recommendation, or favoring by the United States Government or any agency thereof or its contractors or subcontractors.
DATE: Aug 23, 2016
By Julia Raymer at 10:32 am, Aug 23, 2016 Release Approval Date Release Stamp
Approved For Public Release
A-6002-767 (REV 3) RPP-RPT-50703 Rev.01A 8/23/2016 - 10:10 AM 3 of 77
RPP-RPT-50703 Rev.1A
Development of a Thermodynamic Model for the Hanford Tank Waste Operations Simulator (HTWOS)
R Carter Atkins Global, LLC Richland, WA 99354
U.S. Department of Energy Contract DE-AC27-08RV14800
ABSTRACT
Complex equilibria exist between the aqueous phase and solid phases in Hanford waste. Because these solutions contain components at high concentration, it is necessary to obtain accurate parameterizations of water activity for retrieval, transfer, and for the vitrification plant at relevant temperatures and concentrations where storage, processing, and treatment are to be performed. This information can be used to predict identity and concentrations of solid hydrates known to exist in Hanford waste at the same time as aqueous species concentrations. The components included in the thermodynamic model described in this report are those constituents considered most important in Hanford Tank waste, i.e. NaNO2, NaNO3, NaOH, NaAl(OH)4, NaF, Na2CO3, Na2SO4, Na2C2O4, Na2HPO4, Na3PO4, and water. The solid phase components considered are: Al(OH)3, Na2C2O4, Na2CO3·H2O, Na2CO3·7H2O, Na2CO3·10H2O, Na2SO4, Na2SO4·10H2O, NaF, NaF·Na2SO4, Na2HPO4·12H2O, NaNO3·Na2SO4·H2O, NaNO2, NaNO3, Na3PO4·¼NaOH·12H2O, NaF·2Na3PO4·19H2O, and NaAlCO3(OH)2. The thermodynamic model described here is the well-known Pitzer ion-interaction model for calculation of ion activity coefficients and water activity (via the osmotic coefficient) in aqueous multicomponent electrolyte systems. The parameters required by the Pitzer model for the components considered here have been obtained from the open literature. To ensure the final model is self-consistent, these parameters were optimized by fitting the model to solubility data of simple mixtures available in the open literature. This optimized model allows predictions of phase speciation to high ionic strengths and temperatures from 0 to 100 °C. The ultimate goal is to include this thermodynamic model into the Hanford Tank Waste Operations Simulator (HTWOS) to replace existing simple wash and leach factors for the species listed above.
KEY WORDS
Thermodynamics, Pitzer ion-interaction model, water activity, solute activity, molality, ionic strength, solubility, Hanford crystal phases, osmotic coefficient, activity coefficient, HTWOS. RPP-RPT-50703 Rev.01A 8/23/2016 - 10:10 AM 4 of 77
TABLE OF CONTENTS
1 INTRODUCTION ...... 1 2 THERMODYNAMIC MODEL DESCRIPTION...... 3 2.1 EXCESS GIBBS FREE ENERGY...... 3 2.2 MULTICOMPONENT OSMOTIC COEFFICIENT ...... 4 2.3 MULTICOMPONENT ACTIVITY COEFFICIENTS ...... 5 2.4 HIGHER ORDER UNSYMMETRICAL MIXING PARAMETERS...... 6 2.5 TEMPERATURE DEPENDENCE OF THE PITZER PARAMETERS ...... 8 3 GIBBS ENERGY MINIMIZATION ...... 10 3.1 GIBBS ENERGY MINIMIZATION SPREADSHEET (GEMS) ...... 10 3.1.1 GEM Worksheet...... 11 3.1.2 Pitzer Model Worksheet...... 12 3.1.3 Gibbs Energy (Felmy) Worksheet...... 13 3.1.4 Gibbs Energy (Weber) Worksheet ...... 13 3.1.5 Gibbs Energy (HTWOS) Worksheet...... 14 3.1.6 Binary Parameters Worksheet ...... 14 3.1.7 Ternary Parameters Worksheet ...... 14 3.1.8 V & V Worksheet...... 15 4 VERIFICATION OF THE INITIAL PITZER MODEL IMPLEMENTATION...... 16 5 DEVELOPMENT OF THE HTWOS PITZER DATABASE...... 20 5.1 EVALUATION OF SINGLE SOLUTES...... 20
5.1.1 NaNO3 ...... 20
5.1.2 NaNO2 ...... 23 5.1.3 NaOH ...... 25 5.1.4 NaF...... 27 5.1.5 NaCl ...... 27
5.1.6 Na2SO4...... 28
5.1.7 Na2CO3 ...... 30
5.1.8 Na3PO4...... 32
5.1.9 Na2C2O4 ...... 35 5.2 EVALUATION OF SOLUTE MIXTURES...... 36
5.2.1 Na-NO2-NO3-H2O ...... 36
5.2.2 Na-NO3-OH-H2O ...... 37
5.2.3 Na-NO3-F-H2O...... 38
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5.2.4 Na-NO3-C2O4-H2O ...... 38
5.2.5 Na-NO3-CO3-H2O ...... 39
5.2.6 Na-NO2-OH-H2O ...... 39
5.2.7 Na-NO2-CO3-H2O ...... 40
5.2.8 Na-NO2-SO4-H2O...... 40
5.2.9 Na-OH-F-H2O ...... 41
5.2.10 Na-OH-C2O4-H2O ...... 41
5.2.11 Na-OH-CO3-H2O...... 42
5.2.12 Na-OH-SO4-H2O ...... 43
5.2.13 Na-OH-PO4-H2O ...... 43
5.2.14 Na-NO2-PO4-H2O...... 44
5.2.15 Na-SO4-PO4-H2O ...... 45
5.2.16 Na-CO3-PO4-H2O ...... 46
5.2.17 Na-Cl-OH-H2O...... 47
5.2.18 Na-Cl-OH-Al-H2O ...... 47 5.3 DOUBLE SALT SYSTEMS ...... 48
5.3.1 Na-NO3-SO4-H2O...... 49
5.3.2 Na-F-SO4-H2O...... 49
5.3.3 Na-F-PO4-H2O...... 50
5.3.4 Na-CO3-HCO3-H2O...... 50
5.3.5 Na-CO3-SO4-H2O ...... 51 5.4 ADDITIONAL SALT SYSTEMS...... 52
5.4.1 NaAlCO3(OH)2 (Dawsonite) ...... 52 5.4.2 AlOOH (Boehmite) ...... 53 6 CONCLUSIONS ...... 54 7 REFERENCES...... 55 APPENDIX A – COEFFICIENTS FOR GIBBS ENERGY OF FORMATION...... 61 APPENDIX B – BINARY PITZER PARAMETERS...... 63 APPENDIX C – TERNARY PITZER PARAMETERS...... 65 APPENDIX D – VBA CODE LISTING FOR EXCEL FUNCTION ETHETA ...... 68
LIST OF FIGURES
Figure 3-1. GEM Worksheet Layout...... 11 Figure 3-2. Solver Parameters Window...... 12
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Figure 5-1. NaNO3 Osmotic Coefficients at 0 °C...... 21 Figure 5-2. NaNO3 Osmotic Coefficients at 25 °C...... 21 Figure 5-3. NaNO3 Osmotic Coefficients at 50 °C...... 22 Figure 5-4. NaNO3 Osmotic Coefficients at 75 °C...... 22 Figure 5-5. NaNO3 Osmotic Coefficients at 100 °C...... 22 Figure 5-6. Solubility of NaNO₃ in H2O...... 22 Figure 5-7. NaNO2 Osmotic Coefficients at 0 °C...... 24 Figure 5-8. NaNO2 Osmotic Coefficients at 25 °C...... 24 Figure 5-9. NaNO2 Osmotic Coefficients at 50 °C...... 24 Figure 5-10. NaNO2 Osmotic Coefficients at 100 °C...... 24 Figure 5-11. Solubility of NaNO2 in H2O...... 24 Figure 5-12. NaOH Osmotic Coefficients at 0 °C...... 26 Figure 5-13. NaOH Osmotic Coefficients at 25 °C...... 26 Figure 5-14. NaOH Osmotic Coefficients at 40 °C...... 26 Figure 5-15. NaOH Osmotic Coefficients at 70 °C...... 26 Figure 5-16. NaOH Osmotic Coefficients at 100 °C...... 26 Figure 5-17. Solubility of NaF in H2O from 0 to 100 °C...... 27 Figure 5-18. Solubility of NaCl in H2O from 0 to 100 °C...... 28 Figure 5-19. Na2SO4 Osmotic Coefficients at 20 °C...... 29 Figure 5-20. Na2SO4 Osmotic Coefficients at 25 °C...... 29 Figure 5-21. Na2SO4 Osmotic Coefficients at 45 °C...... 29 Figure 5-22. Na2SO4 Osmotic Coefficients at 60 °C...... 29 Figure 5-23. Na2SO4 Osmotic Coefficients at 80 °C...... 29 Figure 5-24. Na2SO4 Osmotic Coefficients at 99.6 °C...... 29 Figure 5-25: Solubility of Na2SO4 in H2O from 0 to 100 °C ...... 30 Figure 5-26: Solubility of Na2CO3 in H2O from 0 to 100 °C...... 32 Figure 5-27. Na2HPO4 Osmotic Coefficients at 0 °C...... 33 Figure 5-28. Na2HPO4 Osmotic Coefficients at 25 °C...... 33 Figure 5-29. Na2HPO4 Osmotic Coefficients at 100 °C...... 33 Figure 5-30. Na2HPO4 Osmotic Coefficients for all the Data...... 33 Figure 5-31: Solubility of Na2HPO4 in H2O from 0 to 100 °C ...... 34 Figure 5-32. Na3PO4 Osmotic Coefficients at 0 °C...... 35 Figure 5-33. Na3PO4 Osmotic Coefficients at 25 °C...... 35 Figure 5-34. Na3PO4 Osmotic Coefficients at 100 °C...... 35 Figure 5-35. Solubility of Na3PO4 in H2O...... 35 Figure 5-36. Solubility of Na2C2O4 in H2O from 0 to 100 °C...... 35 Figure 5-37. Solubilities of NaNO2 and NaNO3 in the NaNO2-NaNO3-H2O System from 0 to 103 °C. .. 37 Figure 5-38. Solubility of NaNO3 in the NaOH-NaNO3-H2O System from 0 to 100 °C...... 37 Figure 5-39. Solubilities of NaF and NaNO3 in the NaF-NaNO3-H2O System at 25 and 50 °C...... 38 Figure 5-40. Solubilities of NaNO3 and Na2C2O4 in the NaNO3-Na2C2O4-H2O System at 20, 50 and 75 °C...... 38 Figure 5-41. Solubilities of NaNO3 and Na2CO3 in the NaNO3-Na2CO3-H2O System at 10, 24.2 and 25 °C...... 39 Figure 5-42. Solubility of NaNO2 in the NaNO2-NaOH-H2O System at 20 and 25 °C...... 40 Figure 5-43. Solubilities of NaNO2 and Na2CO3 in the NaNO2-Na2CO3-H2O System at 20, 23.1 and 25 °C...... 40 Figure 5-44. Solubilities of NaNO2 and Na2SO4 in the NaNO2-Na2SO4-H2O System at 0, 25 and 50 °C...... 41 Figure 5-45. Solubility of NaF in the NaF-NaOH-H2O System from 0 to 94 °C...... 41 Figure 5-46. Solubility of Na2C2O4 in the Na2C2O4-NaOH-H2O System from 0 to 50 °C...... 42
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Figure 5-47. Solubility of Na2CO3 in the Na2CO3-NaOH-H2O System from 0 to 100 °C...... 42 Figure 5-48. Solubility of Na2SO4 in the Na2SO4-NaOH-H2O System from 0 to 100 °C...... 43 Figure 5-49. Solubility of Na3PO4 in the Na3PO4-NaOH-H2O System from 0 to 100 °C...... 44 Figure 5-50 - Solubility of Na3PO4 and NaNO2 in the Na3PO4-NaNO2-H2O System at 25 °C ...... 45 Figure 5-51 - Solubility of Na2HPO4 in Na2SO4 in the Na2HPO4-Na2SO4-H2O System at 25 °C...... 45 Figure 5-52 - Solubility of Na3PO4 in Na2SO4 in the Na3PO4-Na2SO4-H2O System at 25 °C...... 46 Figure 5-53. Solubilities of Na2CO3 and Na3PO4 in the Na2CO3-Na3PO4-H2O System from 0 to 100 °C...... 47 Figure 5-54. Solubility of NaCl in the NaCl-NaOH-H2O System from 0 to 90 °C...... 47 Figure 5-55. Solubility of Al(OH)3 in the NaCl-NaOH-Al(OH)3-H2O System from 6 to 80 °C...... 48 Figure 5-56. Solubility of Al(OH)3 in the NaOH-Al(OH)3-H2O System at 40, 70, and 100 °C...... 48 Figure 5-57. Solubilities of NaNO3 and Na2SO4 in the NaNO3-Na2SO4-H2O System from 0 to 100 °C...... 49 Figure 5-58. Solubilities of NaF and Na2SO4 in the NaF-Na2SO4-H2O System from 0 to 80 °C...... 50 Figure 5-59. Solubilities of NaF and Na3PO4 in the NaF-Na3PO4-H2O System from 25 to 50 °C...... 50 Figure 5-60. Solubilities of Na2CO3 and NaHCO3 in the Na2CO3-NaHCO3-H2O System from 0 to 100 °C...... 51 Figure 5-61 - Solubilities of Na2CO3 and Na2SO4 in the Na2CO3-Na2SO4-H2O System from 15 to 100 °C...... 52
LIST OF TABLES
Table 2-1. Numerical Arrays for Calculating J(x) and J'(x)...... 8 Table 2-2. Debye-Hückel Parameter Coefficients...... 9 Table 4-1. Verification Tests...... 16 Table 4-2. Test 18 Results Comparison for Tank AW-103 at 25 °C...... 17 Table 4-3. Test 19 Results Comparison for Tank AW-103 at 50 °C...... 18 Table 4-4. Comparison of the Solubility Results for the System Na-CO3-PO4-H2O at 25 °C...... 19 Table 5-1. Data Sources for properties of NaNO3...... 20 Table 5-2. Weber Pitzer Parameters and Reduced Chemical Potentials for NaNO3...... 21 Table 5-3. Data Sources for properties of NaNO2...... 23 Table 5-4. Weber Pitzer Parameters and Reduced Chemical Potentials for NaNO2...... 23 Table 5-5. Data Sources for properties of NaOH...... 25 Table 5-6. Weber Pitzer Parameters and Reduced Chemical Potentials for NaOH...... 25 Table 5-7. Data Sources for solubility of NaF in H2O...... 27 Table 5-8. Data Sources for properties of Na2SO4...... 28 Table 5-9. Comparison of Osmotic Coefficients for Na2CO3 from 5 to 45 °C...... 31 Table 5-10. Data Sources for properties of Na2HPO4...... 33 Table 5-11. Data Sources for properties of Na3PO4...... 34 Table 5-12. Solute Mixtures Analyzed and Applicable Range of Temperature...... 36 Table 5-13. Reduced Ideal Chemical Potentials for Dawsonite in the Temperature Range 0 to 100 °C... 53 Table 5-14. Reduced Ideal Chemical Potentials for Boehmite in the Temperature Range 0 to 100 °C. ... 53
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LIST OF TERMS
Abbreviations and Acronyms
DC Dependent Component DSP Disodium Hydrogen Phosphate GEMS Gibbs Energy Minimization Spreadsheet HTWOS Hanford Tank Waste Operations Simulator IAP Ion Activity Product IC Independent Component MSE Mixed Solvent Electrolyte SF Scaling Factor SI Solubility Index TSP Trisodium Phosphate VBA Visual Basic for Applications WTP Hanford Waste Treatment and Immobilization Plant
Units
atm atmosphere oC Celsius J Joules K Kelvin kg kilogram kPa kilopascals m molal mbar millibar mol mole
Definitions
T Absolute Temperature (K) γ Activity coefficient (molal basis) GEX Excess Gibbs free energy I Ionic Strength (molal basis) m Molality Osmotic coefficient (molal basis) Pw Pure water vapor pressure Ω Solubility Index Ps Solution vapor pressure R Universal Gas Constant aw Water activity
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RPP-RPT-50703 Rev. 1A
1 INTRODUCTION This report describes a thermodynamic model for incorporation into the Hanford Tank Waste Operations Simulator (HTWOS) to replace existing simple wash and leach factors. Currently, HTWOS uses these simple wash and leach factors to predict partitioning of chemical species between the liquid and solid phases during retrieval operations in Tank Farms and, in addition, washing and leaching operations in the Hanford Waste Treatment and Immobilization Plant (WTP) (RPP-RPT-17152, Hanford Tank Waste Operations Simulator (HTWOS) Version 6.5 Model Design Document). In order to improve the retrieval, washing and leaching predictions, constituents tracked in HTWOS will be divided into four categories based on relative solubility as described in RPP-PLAN-46002, Wash and Leach Factor Work Plan: Extremely soluble constituents. These constituents are assumed to be in the liquid phase at all times once they are dissolved from saltcake during retrieval. Extremely insoluble constituents. These constituents will continue to use existing simple wash and leach factors, or newer simplified correlations, as so little dissolves into the liquid phase that large errors in relative concentrations will have negligible effects on the accuracy of absolute concentration. Constituents of intermediate solubility. The solubility of these constituents depends highly on waste processing conditions. Their wash and leach factors will be replaced and a more rigorous thermodynamic model will be used to predict their solubility. Kinetic dependent. The solubility of these constituents depends on kinetics, i.e. the amount dissolved or precipitated is a function of time. The thermodynamic model described in this report deals with only those constituents which fall into the intermediate solubility group. These constituents are those in significant concentrations in Hanford waste or deemed important contributors to waste transfer and storage issues, corrosion mitigation, predicted mission length, glass product quality, or all of these. Constituents included are, but not limited to, gibbsite, trisodium phosphate, sodium fluoride, sodium sulfate, sodium oxalate, sodium carbonate. In addition, sodium hydroxide, sodium nitrite and sodium nitrate are included, even though they are highly soluble, as they are the largest contributors to ionic strength. The thermodynamic model chosen is the well-known Pitzer ion-interaction model for mixed electrolytes as found in “Thermodynamics of Electrolytes: IV. Activity and Osmotic Coefficients for Mixed Electrolytes” (Pitzer and Kim 1974) and extended in “The Prediction of Mineral Solubilities in Neutral Waters: The Na-K-Mg-Ca-H-Cl-SO4-OH-HCO3-CO3-CO2-H2O System to High Ionic Strengths at 25 °C” (Harvie et al. 1984); TWRS-PP-94-090, A Chemical Model for the Major Electrolyte Components of the Hanford Waste Tanks. The Binary Electrolytes in the System: Na-NO3-NO2-SO4-CO3-F-PO4-OH- Al(OH)4-H2O; and SAND2009-3115, Implementation of Equilibrium Aqueous Speciation and Solubility (EQ3 type) Calculations into Cantera for Electrolyte Solutions. This model is widely accepted in the scientific community, underpinning many software programs, and has been used to predict Hanford waste speciation to some success in the past. The Pitzer model calculates ion activity coefficients and water activity for a given mixture composition and temperature. To do this requires up to four parameters (known as binary parameters) per solute and requires at least two other parameters (known as mixing parameters) per solute when predicting multicomponent systems. Of the solutes chosen for this application, all have binary and mixing parameters available in the open literature.
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Before the Pitzer model is incorporated into HTWOS, a Microsoft Excel1 based application (hereafter called GEMS) has been developed so that offline testing, verification and validation can be performed. To verify the model was translated into Excel correctly, results from GEMS have been compared to those obtained from GMIN, a Gibbs free energy minimization package developed by Felmy in PNL-7281, GMIN: A Computerized Chemical Equilibrium Model Using a Constrained Minimization of the Gibbs Free Energy, also based on Pitzer’s equations, using the same input compositions and model parameters. Following successful verification, a self-consistent set of Pitzer parameters was generated by optimization against solubility data of simple (binary and ternary) systems available in the open literature and relevant to the constituents of interest for HTWOS. The starting values for these parameters were taken from several sources in the open literature; ORNL/TM-2000/317, Modeling of Sulfate Double-salts in Nuclear Waste; ORNL/TM-2000/348, Waste and Simulant Precipitation Issues; ORNL/TM-2001/102, Thermodynamic Modeling of Savannah River Evaporators; and ORNL/TM-2001/109, Phase Equilibrium Studies of Savannah River Tanks and Feed Streams for the Salt Waste Processing Facility.
1 Excel is a registered trademark of Microsoft Corporation, Redmond, Washington
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2 THERMODYNAMIC MODEL DESCRIPTION
2.1 EXCESS GIBBS FREE ENERGY In order to predict solubility of a salt accurately, knowledge of ion activity coefficients of its constituents is required. For hydrated salts, the activity of water is also required. To calculate ion activity coefficients and water activity, a thermodynamic model is required. The model chosen for implementation in HTWOS is the well-known Pitzer ion-interaction model described first in “Thermodynamics of Electrolytes: I. Theoretical Basis and General Equations” (Pitzer 1973). This model has been extended by several researchers (e.g., Harvie et al. 1984; TWRS-PP-94-090; SAND2009-3115) to include interactions with neutral aqueous species. Pitzer’s model is based on a virial expansion of the excess Gibbs free energy of the solution, which on a ‘per kg of solvent’ basis, is defined as: = (1 − + ln ) (2-1) where GEX is the difference or “excess” in the Gibbs free energy between a real solution and an ideal solution defined on the molality scale, ww is the mass of solvent (usually water) in the solution in th kilograms, mi is the molality of the i ion, is the osmotic coefficient on a molality basis, and γi is the activity coefficient of the ith ion on a molality basis. R is the universal gas constant and T is the absolute temperature. The general expression adopted by Pitzer to represent the excess Gibbs free energy is a combination of the Debye-Hückel theory for long range ionic interactions with a second and third order virial coefficient expansion to account for short range interactions (Pitzer and Kim 1974). Using the notation given by Moffat in SAND2009-3115, the expression is given as: 4 = − ln 1 + √ + 2 + ( ) 3
+ 2Φ + + 2Φ + (2-2) + 2 + 2 + 2 +
+ where is a subscript extending over all anions, extends over all cations, and extends only over all neutral solute molecules. The summations denoted by c