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A-6002-767 (REV 3)
RPP-ENV-58562, Rev. 3
Inventory Data Package for the Integrated Disposal Facility Performance Assessment
Author Name:
K. A. Prindiville
Washington River Protection Solutions, LLC.
Richland, WA 99352 U.S. Department of Energy Contract DE-AC27-08RV14800
EDT/ECN: DRCF UC:
Cost Center: Charge Code:
B&R Code: Total Pages: 118
Key Words: Performance Assessment, Integrated Disposal Facility, IDF, MLLW, LLW, HLW, Hanford Tank Waste
Operations Simulator, HTWOS, Performance Assessment, LAW melter, ILAW glass, Effluent Treatment
Facility, ETF, Secondary Solid Waste, SSW, FFTF
Abstract: This document provides estimates of the waste inventories and associated waste volumes for each of the
waste streams that are planned to be disposed of at the Integrated Disposal Facility (IDF) for purpose of
evaluating the long-term impact on human health and the environment in the 2017 IDF Performance
Assessment (PA).
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.
Release Approval Date Release Stamp
Approved For Public Release
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By Janis D. Aardal at 11:37 am, May 09, 2016
May 09, 2016DATE:
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Tank Farm Contractor (TFC) RECORD OF REVISION
(1) Document Number: Page ___2
RPP-ENV-58562 Rev. 3
A-6003-835 (REV 5)
Change Control Record (3)
Revision (4) Description of Change – Replace, Add, and Delete Pages Authorized for Release
(5) Author. (print/sign/date) (6) Resp. Mgr. (print/sign/date)
recommendations apply to “as-generated” waste volumes to determine “as-disposed” of waste volumes.
Section 10.0 (now Section 9.0)
• Updated inventory to reflect rerun of HTWOS and addition/distribution of HTWOS “Total Accumulation” inventory to both IDF and non-IDF waste stream mass balance.
• Updated inventory tables to include detailed inventory of WTP SSW streams to include HEPA filters, ion exchange resin, HLW and LAW carbon adsorber beds, HLW silver mordenite absorbent, and other debris.
Added Appendix A-detailed inventory tables for each run case
Added Appendix B- to document calculation checks and numeric table checks
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RPP-ENV-58562
Revision 3
Inventory Data Package for the Integrated Disposal Facility Performance Assessment
K. A. Prindiville
Washington River Protection Solutions, LLC
Date Published
May 2016
Prepared for the U.S. Department of Energy
Office of River Protection
Contract No. DE-AC27-08RV14800
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TABLE OF CONTENTS
1.0 INTRODUCTION ........................................................................................................... 1-1
2.0 INTEGRATED DISPOSAL FACILITY WASTE STREAMS SOURCES AND
TERMINOLOGY ............................................................................................................ 2-1
3.0 INTEGRATED DISPOSAL FACILITY WASTE STREAM DESCRIPTIONS ............ 3-1
3.1 WASTE TREATMENT AND IMMOBILIZATION PLANT-
GENERATED WASTE ....................................................................................... 3-1
3.1.1 Immobilized Low-Activity Waste Glass ................................................. 3-1
3.1.2 Low-Activity Waste Melters.................................................................... 3-1
3.1.3 Secondary Solid Waste ............................................................................ 3-2
3.1.4 Effluent Treatment Facility-Generated Secondary Solid Waste .............. 3-2
3.2 NON-WASTE TREATMENT AND IMMOBILIZATION PLANT
GENERATED WASTE ....................................................................................... 3-3
3.2.1 Fast Flux Test Facility Decommissioning Waste .................................... 3-3
3.2.2 Secondary Waste Management Low-Level Waste and Mixed
Low-Level Waste ..................................................................................... 3-4
3.2.3 Onsite Non-CERCLA Non-Tank Low-Level Waste and Mixed
Low-Level Waste ..................................................................................... 3-4
4.0 TANK WASTE INVENTORY ....................................................................................... 4-1
4.1 BEST-BASIS INVENTORY BACKGROUND .................................................. 4-1
4.2 BEST-BASIS INVENTORY UNCERTAINTY ................................................. 4-2
4.2.1 Total Best-Basis Inventory Uncertainty ................................................... 4-2
4.2.2 Tank and Waste Phase Uncertainties ....................................................... 4-2
4.3 BEST-BASIS INVENTORY COMPARISON.................................................... 4-3
4.4 TANK INVENTORY HISTORY OF TECHNETIUM-99 AND
IODINE-129 ...................................................................................................... 4-11
4.4.1 Technetium-99 Tank Waste Inventory History ..................................... 4-11
4.4.2 Iodine-129 Tank Waste Inventory History ............................................ 4-14
5.0 HANFORD TANK WASTE OPERATIONS SIMULATOR ......................................... 5-1
5.1 HANFORD TANK WASTE OPERATIONS SIMULATOR
BACKGROUND ................................................................................................. 5-1
5.2 HANFORD TANK WASTE OPERATIONS SIMULATOR
UNCERTAINTY AND LIMITATIONS ............................................................. 5-1
5.3 HANFORD TANK WASTE OPERATIONS SIMULATOR
COMPARISON ................................................................................................... 5-4
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6.0 WASTE TREATMENT AND IMMOBILIZATION PLANT GENERATED
WASTE INVENTORY ESTIMATES—RESULTS ....................................................... 6-1
6.1 THE ENVIRONMENTAL IMPACT STATEMENT AND HANFORD
TANK WASTE OPERATIONS SIMULATOR CASES INVENTORY
ESTIMATES........................................................................................................ 6-1
6.2 WASTE TREATMENT AND IMMOBILIZATION PLANT
SECONDARY SOLID WASTE STREAM PARTITION FRACTIONS ........... 6-7
7.0 NON-WASTE TREATMENT AND IMMOBILIZATION PLANT-GENERATED
WASTE INVENTORY ESTIMATES ............................................................................ 7-1
7.1 FAST FLUX TEST FACILITY DECOMMISSIONING WASTE
INVENTORY ESTIMATE ................................................................................. 7-1
7.2 SECONDARY WASTE MANAGEMENT LOW-LEVEL WASTE
AND MIXED LOW-LEVEL WASTE INVENTORY ESTIMATE ................... 7-1
7.3 ONSITE NON-CERCLA NON-TANK LOW-LEVEL WASTE AND
MIXED LOW-LEVEL WASTE .......................................................................... 7-3
8.0 INTEGRATED DISPOSAL FACILITY WASTE VOLUME METHODOLOGY ........ 8-1
8.1 IMMOBILIZED LOW-ACTIVITY WASTE GLASS WASTE
VOLUME ESTIMATES ..................................................................................... 8-1
8.2 AS-GENERATED WASTE TREATMENT AND IMMOBILIZATION
PLANT SECONDARY SOLID WASTE VOLUME ESTIMATES................... 8-3
8.3 BACKGROUND-INDUSTRY STANDARDS FOR WASTE
TREATMENT ..................................................................................................... 8-5
8.3.1 Low-Level Waste ..................................................................................... 8-5
8.3.2 Mixed Low-Level Waste ......................................................................... 8-5
8.4 WASTE TREATMENT AND IMMOBILIZATION PLANT
SECONDARY SOLID WASTE TREATMENT AND DISPOSAL
CONSIDERATIONS AND ASSUMPTIONS .................................................... 8-6
8.5 LOW-ACTIVITY WASTE MELTER VOLUME ESTIMATES ....................... 8-8
8.6 EFFLUENT TREATMENT FACILITY-GENERATED SECONDARY
SOLID WASTE ................................................................................................... 8-9
8.7 SECONDARY WASTE MANAGEMENT LOW-LEVEL WASTE
AND MIXED LOW-LEVEL WASTE VOLUME ESTIMATES ..................... 8-11
8.8 FAST FLUX TEST FACILITY DECOMMISSIONING WASTE
DISPOSAL VOLUME ESTIMATE.................................................................. 8-11
8.9 AS-GENERATED ONSITE NON-CERCLA NON-TANK LOW-
LEVEL WASTE AND MIXED LOW-LEVEL WASTE VOLUME
ESTIMATES...................................................................................................... 8-12
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9.0 SUMMARY OF RESULTS ............................................................................................ 9-1
9.1 INTEGRATED DISPOSAL FACILITY WASTE FORMS BASED ON
HANFORD TANK WASTE OPERATIONS SIMULATOR RUN
CASES ................................................................................................................. 9-1
9.1.1 Iodine-129 Variations (Figure 9-1 and Figure 9-2) ................................. 9-8
9.1.2 Technetium-99 Variations (Figure 9-3 and Figure 9-4) ........................ 9-11
10.0 DATA QUALITY ASSURANCE FOR THE INTEGRATED DISPOSAL
FACILITY INVENTORY DATA PACKAGE ............................................................. 10-1
11.0 REFERENCES .............................................................................................................. 11-1
LIST OF FIGURES
Figure 2-1. Schematic Showing Generation and Disposal Pathway for Mixed Low-Level
Waste and Low-Level Waste Going to the Integrated Disposal Facility. ................ 2-2
Figure 2-2. Waste Treatment and Immobilization Plant-Generated Waste Streams Going to
Integrated Disposal Facility. .................................................................................... 2-4
Figure 4-1. Published Technetium Inventories in Hanford Tank Waste (Section 4.4.1).......... 4-12
Figure 4-2. Published Iodine-129 Inventories in Hanford Tank Waste (Section 4.4.2). .......... 4-12
Figure 5-1. Hanford Tank Waste Operations Simulator Flow Sheet. ......................................... 5-2
Figure 5-2. Technetium-99 Comparison using Tank Closure and Waste Management
Environmental Impact Statement Partitioning Fractions. ........................................ 5-7
Figure 5-3. Iodine-129 Comparison. ........................................................................................... 5-8
Figure 6-1. Tank Closure Alternative 2B Flowsheet from the Tank Closure and Waste
Management Environmental Impact Statement. ...................................................... 6-2
Figure 6-2. Case 7 – Current Information Case Flowsheet. ....................................................... 6-3
Figure 6-3. Case 8B – Technetium-99 Removal from Low-Activity Waste Vitrification
Off-Gas Condensate Flowsheet. ............................................................................... 6-4
Figure 6-4. Case 9 – Removal of Low-Activity Waste Pretreatment System Flowsheet. .......... 6-5
Figure 6-5. Case 10A and 10B – Low and Medium Efficiency Recycle. .................................. 6-6
Figure 9-1. Iodine-129 Distributions in Integrated Disposal Facility Waste Forms................... 9-9
Figure 9-2. Iodine-129 Inventory in Integrated Disposal Facility Waste Forms. ..................... 9-10
Figure 9-3. Technetium-99 Distributions in Integrated Disposal Facility Waste Forms. ......... 9-12
Figure 9-4. Technetium-99 Inventory in Integrated Disposal Facility Waste Forms. .............. 9-13
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LIST OF TABLES
Table 2-1. Integrated Disposal Facility Waste Stream Terminology. ........................................ 2-1
Table 4-1. Best-Basis Inventory Comparison. ............................................................................ 4-5
Table 4-2. Hanford Tank Waste Historical Inventories for Technetium-99 and Iodine-129. .... 4-6
Table 5-1. Comparison of Hanford Tank Waste Operations Simulator Partitioning Fractions
from the Tank Closure and Waste Management Environmental Impact
Statement versus Current Hanford Tank Waste Operations Simulator
Partitioning Fractions. ............................................................................................... 5-5
Table 6-1. 10-010 Partitioning Fractions for Waste Treatment and Immobilization Plant
Secondary Solid Waste Streams. ............................................................................... 6-8
Table 6-2. Hanford Tank Waste Operations Simulator Partitioning Fractions for Waste
Treatment and Immobilization Plant Secondary Solid Waste Streams. .................... 6-8
Table 6-3. Run Case 7 Contaminant Inventory for Waste Treatment and Immobilization
Plant Secondary Solid Waste Streams using 10-010 Partitioning Fractions. .......... 6-10
Table 6-4. Run Case 7 Contaminant Inventory for Waste Treatment and Immobilization
Plant Secondary Solid Waste Streams using Hanford Tank Waste Operations
Simulator Partitioning Fractions. ............................................................................ 6-10
Table 7-1. Fast Flux Test Facility Decommissioning Inventory Estimates for Waste Going
to Integrated Disposal Facility. ................................................................................. 7-1
Table 7-2. Secondary Waste Management Low-Level Waste and Mixed Low-Level Waste
Inventory Estimates for Waste Going to Integrated Disposal Facility. ..................... 7-2
Table 7-3. Onsite Non-CERCLA Non-Tank Low-Level Waste and Mixed Low-Level
Waste Radioactive Constituents of Potential Concern Inventory. ............................ 7-4
Table 7-4. Onsite Non-CERCLA Non-Tank Low-Level Waste and Mixed Low-Level
Waste Chemical Constituents of Potential Concern Inventory. ................................ 7-5
Table 8-1. Volume Estimates for Immobilized Low-Activity Waste Glass. .............................. 8-2
Table 8-2. Volume Estimates for Waste Treatment and Immobilization Plant Secondary
Solid Waste Streams. ................................................................................................. 8-4
Table 8-3. Volume Estimates for Low-Activity Waste Melters and Residual Glass Volume. .. 8-8
Table 8-4. Effluent Treatment Facility-Generated Secondary Solid Waste Disposal Volume
Estimates. ................................................................................................................ 8-10
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Table 8-5. As-Generated Secondary Waste Management Waste Volume Estimates. .............. 8-11
Table 8-6. Fast Flux Test Facility Decommissioning Disposal Waste Volume Estimate. ....... 8-11
Table 8-7. Onsite Non-CERCLA Non-Tank Low-Level Waste and Mixed Low-Level
Waste As-Generated Volume Estimates. ................................................................ 8-12
Table 9-1. Summary of Radionuclide Constituents Inventories and Waste Form
Distributions Resulting from Hanford Tank Waste Operations
Simulator Run Cases (November 2014 Best-Basis Inventory
with radionuclides decayed to January 2008). .......................................................... 9-3
Table 9-2. Summary of Chemical Constituent Inventories and Waste Form Distributions
Resulting from Hanford Tank Waste Operations Simulator Runs. ........................... 9-5
Table 9-3. Tank Closure Alternative 2A Radioactive Constituents of Potential Concern
Balance. ..................................................................................................................... 9-6
Table 9-4. Tank Closure Alternative 2A Chemical Constituents of Potential Concern
Balance. ..................................................................................................................... 9-7
Table 10-1. Source Data Quality Assurance. ............................................................................ 10-1
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LIST OF APPENDIX A TABLES
Table A-1. Run Case 7 Radionuclides. ...................................................................................... A-3
Table A-2. Run Case 7 Chemicals. ............................................................................................ A-5
Table A-3. Run Case 8B Radionuclides. ................................................................................... A-7
Table A-4. Run Case 8B Chemicals. ......................................................................................... A-9
Table A-5. Run Case 9 Radionuclides. .................................................................................... A-11
Table A-6. Run Case 9 Chemicals. .......................................................................................... A-13
Table A-7. Run Case 10A Radionuclides. ............................................................................... A-15
Table A-8. Run Case 10A Chemicals. ..................................................................................... A-17
Table A-9. Run Case 10B Radionuclides. ............................................................................... A-19
Table A-10. Run Case 10B Chemicals. ................................................................................... A-21
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LIST OF TERMS
BBI Best-Basis Inventory
CERCLA Comprehensive Environmental Response, Compensation, and Liability Act
of 1980
CH Contact Handled
COPC constituent of potential concern
CS Caustic Scrubber
DFLAW Direct Feed Low Activity Waste
DOE U.S. Department of Energy
DKPRO Computer code for radioactive decay (DK) and processing (PRO)
DST double-shell tank
Ecology State of Washington Department of Ecology
EMF Effluent Management Facility
ETF Effluent Treatment Facility
FFTF Fast Flux Test Facility
HDW Hanford Defined Waste (model)
HEPA High-Efficiency Particulate Air (filter)
HLW High-Level Waste
HOG High-Level Waste Off-Gas
HTWOS Hanford Tank Waste Operations Simulator
IDF Integrated Disposal Facility
IHLW Immobilized High-Level Waste
ILAW Immobilized Low-Activity Waste
IX Ion Exchange (resin)
LAWPS Low-Activity Waste Pretreatment System
LAW Low-Activity Waste
LDR Land Disposal Restriction
LERF Liquid Effluent Retention Facility
LLW Low-Level Waste
LOG Low-Activity Waste Off-Gas
MLLW Mixed Low-Level Waste
NEPA National Environmental Policy Act of 1969
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ORIGEN2 Oak Ridge Isotope Generation and Depletion Code
ORP DOE Office of River Protection
PA Performance Assessment
PNNL Pacific Northwest National Laboratory
PT Pretreatment
RCB Reactor Containment Building
RCRA Resource Conservation and Recovery Act of 1976
RSD Relative Standard Deviation
RPP River Protection Project
SALDS State-Approved Land Disposal Site
SBS Submerged Bed Scrubber
SLAW Supplemental Low-Activity Waste
SLOG Supplemental Low-Activity Waste Off-Gas
SST single-shell tank
SSW Secondary Solid Waste
TC&WM EIS Tank Closure and Waste Management Environmental Impact Statement
TRAC Track Radioactive Constituents computer code
TRU transuranic
TWINS Tank Waste Information Network System
VSL Vitreous State Laboratory
WESP Wet Electrostatic Precipitator
WRAP Waste Receiving and Processing (facility)
WRPS Washington River Protection Solutions
WTP Waste Treatment and Immobilization Plant
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1.0 INTRODUCTION
This document provides the current estimates of the waste inventories to be disposed in the
Integrated Disposal Facility (IDF) for purposes of evaluating the long-term impact on human
health and the environment in the 2017 IDF Performance Assessment (PA).
Release of contaminants from the waste in a disposal facility into the environment depends on a
number of factors. The most important factors are the inventory of contaminants in a particular
waste form and the waste form release behavior. A PA for a proposed disposal facility evaluates
the breakdown of the waste form, the release of contaminants into the environment, and the
eventual impact of the contaminants, such as groundwater concentrations. The PA provides
information to allow decision makers to define constraints on the disposal facility design,
operation, acceptable waste forms, acceptable waste form inventories, and other criteria to
provide reasonable assurance that the performance objectives of the disposal facility will be met.
This document does not define exactly what the inventory of contaminants will be in each waste
form to be disposed at the IDF. Instead, it proposes a range of inventories that might occur,
realizing that the Waste Treatment and Immobilization Plant (WTP) process flowsheet may
continue to develop over time given ongoing regulatory discussions and technical decisions.
Separate documents will propose a range of waste release behaviors to be evaluated for each
waste form. Evaluating a range of values for each key parameter provides insight into how the
parameters interact. For example, high inventories of key contaminants may be placed into more
robust waste forms. Less robust waste forms may still be allowed, but limits must be determined
for the inventory in these waste forms.
This document has considered inventory ranges for particular waste forms based on operating
scenarios that are not anticipated from the current flowsheets and that may lead to unacceptable
results (i.e., performance objectives may not be met). The purpose in proposing these ranges is
to understand how changes in key parameters affect the outcome over a wide range of values.
This understanding allows for the development of waste acceptance criteria informed by
modeled performance of the disposal facility.
Specifically, five run cases (7, 8B, 9, 10A, and 10B) were developed to explore the range of
inventory in waste streams going to the IDF that result from processing tank waste through the
WTP Facility using different process flowsheet assumptions. In the interest of testing the IDF
system, each case was designed to produce a range of distributions of 99Tc and 129I in glass and
non-glass waste forms. Although Cases 7 and 9 may be more likely representations of the WTP
flowsheet configuration, Cases 10A and 10B are unlikely cases that were developed to test the
limits of 99Tc and 129I loadings in non-glass waste forms against established waste form
performance objectives. For Cases 10A and 10B, process simulators were used to partition
inventory between the different waste forms using contrived process flowsheet configurations to
test the upper limits of what waste form concentrations the IDF could receive and still meet the
performance criteria of the facility. These cases are included to help establish waste acceptance
criteria for specific waste forms.
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Collectively, the five cases serve as a starting point for gaining an understanding of the IDF
disposal system considering all the uncertainties associated with the IDF waste forms. Other run
cases are expected to evolve based on the knowledge gained from these initial run cases and the
maturity of the WTP process flowsheet. The five run cases presented here were repeated with
updated assumptions from the previous version of this document including corrections to the
off-gas reactions and stream splits which have been incorporated into Hanford Tank Waste
Operations Simulator (HTWOS) Version 8.1 (RPP-17152, Rev. 12, “Hanford Tank Waste
Operations Simulator (HTWOS) Version 8.1 Model Design Document”). Notable changes from
the previous version include the splits associated with Hg and 14C in the Low-Activity Waste
(LAW) off-gas system as well as the split associated with 137Cs based on a correction to the
elution factor applied to the cesium ion exchange resin.
This document also recognizes that tank waste compositions are complex and that there are
multiple sources of uncertainty associated with the estimated inventory for each waste stream
modeled. These uncertainties include tank waste composition and inventory uncertainties, WTP
process and operational uncertainties, and model partitioning uncertainties. Evaluating a range
of values helps identify the parameters which have greatest impact on the outcome, and where
improved information (e.g., additional measurements or process definition) may be needed.
The 2017 IDF PA will evaluate a range of contaminant inventories associated with a range of
waste form behaviors. The expected outcome is an understanding of the areas within those
ranges that lead to acceptable outcomes.
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2.0 INTEGRATED DISPOSAL FACILITY WASTE STREAMS SOURCES AND
TERMINOLOGY
The IDF is planning to receive Mixed Low-Level Waste (MLLW) and Low-Level Waste (LLW)
generated by the WTP as a result of the vitrification process. Those waste streams include:
Immobilized Low-Activity Waste (ILAW) glass
Low-Activity Waste (LAW) melters
Secondary solid waste (SSW)
Effluent Treatment Facility (ETF)-generated SSW.
Additional waste streams would be generated that are not a result of the WTP process. These
waste streams would also be disposed of at the IDF and include:
Fast Flux Test Facility (FFTF) decommissioning waste
Secondary waste management LLW and MLLW
Onsite Non-Comprehensive Environmental Response, Compensation, and Liability Act
of 1980 (CERCLA) non-tank LLW and MLLW.
The use of common and consistent terms when referring to these IDF waste streams is a key
consideration for all project efforts associated with the analysis or discussion of waste disposal at
the IDF. Table 2-1 establishes the waste stream names consistently applied in this document.
Additionally, Figures 2-1 and 2-2 provide information related to the generation and disposal
pathways for each of these waste streams.
Table 2-1. Integrated Disposal Facility Waste Stream Terminology.
Waste Stream Names
WTP-Generated Waste Streams Non-WTP-Generated Waste Streams
Immobilized Low-Activity Waste glass Secondary Waste Management LLW and MLLW
Low-Activity Waste melters Fast Flux Test Facility decommissioning waste
Secondary solid waste Onsite Non-CERCLA non-tank LLW and
MLLW Effluent Treatment Facility-generated secondary solid waste
CERCLA = Comprehensive Environmental Response, Compensation, and Liability Act of 1980
LLW = Low-Level Waste
MLLW = Mixed Low-Level Waste
WTP = Waste Treatment and Immobilization Plant
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Figure 2-1. Schematic Showing Generation and Disposal Pathway for Mixed Low-Level
Waste and Low-Level Waste Going to the Integrated Disposal Facility.
CERCLA = Comprehensive Environmental Response, Compensation, and Liability Act of 1980
ETF = Effluent Treatment Facility LAW = Low-Activity Waste
FFTF = Fast Flux Test Facility LLW = Low-Level Waste
IDF = Integrated Disposal Facility MLLW = Mixed Low-Level Waste
ILAW = Immobilized Low-Activity Waste WTP = Waste Treatment and Immobilization Plant
Prior to disposal, these waste streams would be treated appropriately to meet Land Disposal
Restrictions (LDR)1 and waste acceptance criteria for the IDF. The resulting “as disposed”
1 Congress created the LDR program on November 8, 1984 as part of the Hazardous and Solid Waste Amendments
to the Resource Conservation and Recovery Act of 1976. This law prohibits the land disposal of untreated
hazardous wastes. It required the U.S. Environmental Protection Agency to specify either concentration levels or
methods of treatment for hazardous constituents to either substantially decrease the toxicity of a waste or decrease
the likelihood that contaminants would migrate from a waste and cause contamination of land and groundwater.
The U.S. Environmental Protection Agency responded
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waste forms would be ILAW glass, cementitious (grouted), or compacted waste forms as shown
in Figure 2-1. Alternative treatment methods to grouting may be viable for some secondary
wastes. On a case-by-case basis, modeling assumptions for specific waste streams were
developed from existing practices at the Hanford Site or based on consultation with subject
matter experts.
By establishing the LDR program found in Title 40, Code of Federal Regulations, Part 268, “Land Disposal
Restrictions.” The LDR program identifies treatment standards for hazardous wastes and specifies requirements
that generators, transporters, and owners or operators of treatment, storage, and disposal facilities that manage
restricted wastes destined for land disposal must meet.
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Figure 2-2. Waste Treatment and Immobilization Plant-Generated Waste Streams Going to Integrated Disposal Facility.
ETF = Effluent Treatment Facility ILAW = Immobilized Low-Activity Waste LERF = Liquid Effluent Retention Facility
HLW = High-Level Waste LAW = Low-Activity Waste PT = Pretreatment
IDF = Integrated Disposal Facility LAWPS = Low-Activity Waste Pretreatment System WTP = Waste Treatment and Immobilization Plant
Tanks
Off-gas liquids
WTP
Pretreatment
Processes
(Includes WTP
PT and LAWPS) HLW
Vitrification
Process
LAW
Vitrification
Process
LERF/ETF
ETF-Generated Secondary
Solid Waste to the IDF
Secondary Solid Waste to
the IDF
ILAW Glass and LAW
Melters to the IDF
HLW Melters to onsite
storage
HLW Glass to offsite disposal
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3.0 INTEGRATED DISPOSAL FACILITY WASTE STREAM DESCRIPTIONS
3.1 WASTE TREATMENT AND IMMOBILIZATION PLANT-GENERATED
WASTE
To provide an understanding of the relationship between WTP operations and the resulting
WTP-generated waste streams that will be disposed of at the IDF, a simplification of the WTP
process flowsheet is presented in Figure 2-2. Note that the vitrified High-Level Waste (HLW)
glass and HLW melters shown in this figure will not be disposed of at the IDF. Also note that
non-WTP-generated wastes that will be disposed of at the IDF are not shown in Figure 2-2 and
are discussed separately in Section 3.2. A detailed description of the WTP-generated waste
streams including their sources is provided in Sections 3.1.1 through 3.1.4.
Contaminant inventories for the different waste streams produced at the WTP and disposed of at
the IDF over the life of the waste treatment mission were developed from process modeling
using HTWOS. HWTOS was run with different starting conditions and process flow sheet
assumptions to generate a range of inventory values for the different waste streams to support the
2017 IDF PA analysis.
3.1.1 Immobilized Low-Activity Waste Glass
In accordance with 78 FR 75913, “Final Tank Closure and Waste Management Environmental
Impact Statement for the Hanford Site Record of Decision,” the U.S. Department of Energy
(DOE) has implemented Tank Closure Alternative 2B, without supplemental treatment and WTP
without 99Tc removal in the WTP Pretreatment Facility2. The primary waste form for all tank
waste processed at WTP would be an ILAW or Immobilized High-Level Waste (IHLW) glass
waste form. The resulting ILAW glass containers would be disposed of at the IDF while the
IHLW glass canisters would be stored onsite until an offsite geologic repository is identified.
3.1.2 Low-Activity Waste Melters
Spent or failed LAW melters from WTP operations are expected to be MLLW and would also be
disposed of at the IDF. To meet Resource Conservation and Recovery Act of 1976 (RCRA)
LDR requirements, spent or failed LAW melters may be required to be void filled with grout or
macroencapsulated prior to disposal (RPP-RPT-58204, “Spent/Failed Low-Activity Waste
Melter Transport System Evaluation Report”). Additionally, the DOE/EIS-0391, “Final Tank
Closure and Waste Management Environmental Impact Statement for the Hanford Site,
Richland, Washington” (TC&WM EIS) analysis assumed that each LAW melter would be
packaged in an overpack prior to disposal at the IDF.
2 This decision is consistent with 62 FR 8693, “Record of Decision for the Tank Waste Remediation System,
Hanford Site, Richland, WA,” which was not amended in this area as part of the TC&WM EIS Record of
Decision.
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3.1.3 Secondary Solid Waste
SSW is generated as the result of WTP operations. It includes low-level and mixed low-level
radioactive debris and non-debris waste such as melter consumables, failed process components,
analytical laboratory waste, spent resins, spent carbon adsorbent, high-efficiency particulate air
(HEPA) filters, and other process-related waste. Compared to other WTP SSW, the HEPA
filters, spent Ion Exchange (IX) resins, spent carbon adsorber beds, and HLW silver mordenite
absorbent are expected to contain disproportionate amounts of key radionuclides. These MLLW
streams will require different treatment methods (based on contaminant types and levels) to meet
LDR requirements prior to disposal at the IDF. All SSW deemed as LLW would be packaged
and stabilized (grouted) or compacted prior to being disposed of at the IDF.
3.1.4 Effluent Treatment Facility-Generated Secondary Solid Waste
ETF-generated SSW results from treating secondary liquid waste from the 242-A evaporator, the
retrieval of Contact Handled (CH)-transuranic (TRU) tanks, and from WTP operations which
includes low-level and mixed low-level liquid effluent from the melter primary off-gas treatment
system, the LAW vitrification secondary off-gas/vessel vent treatment system, process vessel
washes, floor drains, sumps, and vessel vent header drains. In addition, liquid waste from
Pretreatment Facility sources such as the radioactive liquid disposal vessels and tanks including
process condensates from evaporators, caustic waste from the LAW caustic scrubber, and spent
reagents from the resin addition process would be routed to the Liquid Effluent Retention
Facility (LERF)/ETF for treatment (24590-WTP-RPT-PT-02-005, “Flowsheet Bases,
Assumptions, and Requirements”). For analysis purposes, these liquid waste streams were
assumed to be representative of the ETF-generated SSW received at the IDF3.
The current ETF treatment process is similar to the process that existed when the TC&WM EIS
analysis was performed. Therefore, the differences in the fraction of mobile radionuclides such
as 99Tc and 129I that volatilize and are captured in the liquid off-gas system and ultimately end up
in the ETF-generated SSW is primarily due to changes in the inventory estimate and changes in
the handling of recycle streams at WTP. The earlier HTWOS model that was used in the
TC&WM EIS had a simple recycle scheme for the LAW melter off-gas [Figure D-8 in
RPP-17152, Rev. 1, “Hanford Tank Waste Operations Simulator (HTWOS) Model Design
Description”]. The more recent model (Figure C-15 in RPP-17152, Rev. 12) recycles liquid
effluents to more locations for more effective management of the effluents.
After treatment at the ETF, the liquid portion of the treated waste stream would be disposed of at
the State-Approved Land Disposal Site (SALDS) while the byproduct waste generated from the
ETF solidification process would be packaged and disposed of at the IDF as ETF-generated
SSW. This waste stream originating from the WTP operations is often referred to as WTP
secondary liquid waste.
3 Although leachate from the Mixed Waste Trench and other miscellaneous sources are planned for disposal at the
IDF as part of ETF-generated SSW, the expected radionuclide concentrations and projected waste stream volumes
are assumed insignificant compared to the contributions from WTP operations (RPP-SPEC-43722, “Secondary
Liquid Waste Treatment Plant Project (T3W08) System Specification”). Additionally, IDF leachate contributions
are not included to avoid double counting of inventory in the 2017 IDF PA analysis.
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The high temperatures associated with the LAW vitrification process could cause volatilization
of mobile radionuclides such as 99Tc and 129I that would not be captured in the liquid off-gas
treatment system and would ultimately end up in ETF-generated SSW. Since the fraction of
these constituents ending up in the final waste form is difficult to predict, a wide range of glass
retentions have been proposed to test the limits of 99Tc and 129I loadings in cementitious waste
forms against established waste form performance characteristics.
3.2 NON-WASTE TREATMENT AND IMMOBILIZATION PLANT GENERATED
WASTE
Contaminant inventories associated with the disposal of non-WTP LLW and MLLW (see
Section 7.0) were based on the inventories presented in Appendix D of the TC&WM EIS for
each of these waste streams. Waste sources based on forecasts developed for the TC&WM EIS
have not been updated so that the information included in the TC&WM EIS represents the best
available source for this expected inventory.
3.2.1 Fast Flux Test Facility Decommissioning Waste
In accordance with 78 FR 75913, DOE selected FFTF Alternative 2 Entombment, which would
remove all above-grade structures, including the reactor building. Below-grade structures would
remain in place and be filled with grout to immobilize the remaining radioactive and hazardous
constituents, then covered with a RCRA-compliant barrier.
In accordance with FFTF Alternative 2 Entombment, the remote-handled special components
would be treated at Idaho National Laboratory and returned to the Hanford Site for disposal.
A description of the proposed remote treatment process is included in DOE/EA-01386, “Final
Environmental Assessment for the Remote-handled Waste Disposition Project.”
Bulk sodium inventories would be treated and stored at Hanford for use at the WTP.
Sodium residuals from FFTF components, (e.g., the reactor and miscellaneous traps), would also
be disposed of at the IDF. Table D-80 of the TC&WM EIS reports inventory contributions from
approximately 4,000 gal of sodium residuals.
In addition to sodium residuals, the FFTF secondary waste under the Entombment Alternative
includes:
Demolition waste from the main Reactor Containment Building and Buildings 491E and
491W that cannot be consolidated in below-grade spaces
Radioactive and hazardous materials from other ancillary buildings
The reactor vessel, piping systems, and tanks (drained to the extent practicable of liquid
sodium) that would not fit in below-grade spaces
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Solid waste resulting from waste processing.
3.2.2 Secondary Waste Management Low-Level Waste and Mixed Low-Level Waste
Secondary waste includes workers’ personal protective equipment, tools, and other contaminated
materials from tank farm operations, as well as:
Secondary LLW and MLLW from operation of LLBG 218-W-5, trenches 31 and 34
Secondary LLW and MLLW from operation of the Waste Receiving and Processing
Facility (WRAP)
Secondary LLW and MLLW from operation of the T Plant complex.
3.2.3 Onsite Non-CERCLA Non-Tank Low-Level Waste and Mixed Low-Level Waste
Onsite non-CERCLA non-tank LLW and MLLW includes solid wastes from onsite generators
such as:
Central Waste Complex
Plutonium Finishing Plant
T Plant Complex
Waste Encapsulation and Storage Facility
Waste Receiving and Processing Facility
Groundwater sampling activities
Pacific Northwest National Laboratory (PNNL)
Cold Vacuum Drying Facility
Canister Storage Building
Liquid Waste Processing Facilities (LERF, ETF, SALDS, and Treated Effluent Disposal
Facility).
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4.0 TANK WASTE INVENTORY
For tank waste processed by WTP, the Best-Basis Inventory (BBI) provides the official tank
waste inventory estimates for 177 single-shell tanks (SSTs) and double-shell tanks (DSTs) at the
Hanford Site (RPP-7625, “Guidelines for Updating Best-Basis Inventory”). The BBI is included
in the Tank Waste Information Network System (TWINS) database that stores and provides all
official tank sample/characterization data and other information related to the SSTs and DSTs at
the Hanford Site.
Note that recently completed and planned tank sampling events are reported in RPP-26781,
“Tank Operations Contractor Sampling Projections for FY2016 through FY2020” (which is
updated on an annual basis). The BBI is maintained through quarterly updates which would
include any new tank sample data as applicable in accordance with BBI protocols.
4.1 BEST-BASIS INVENTORY BACKGROUND
BBI estimates are available for each individual waste phase in a tank. These waste phases
include supernate, saltcake solids, saltcake liquid, sludge solids, sludge liquid, and retained gas.
The BBI provides inventory estimates for each standard BBI constituent (25 chemicals and
46 radionuclides) by using:
Sample data
Process knowledge calculations
Waste-type templates based on sample data, and
Hanford Defined Waste (HDW) computer model estimates (RPP-19822, “Hanford
Defined Waste Model – Revision 5.0”).
Sample data are the preferred source of waste concentration information for the BBI. If sample
data are not available, then the “best available” information means process knowledge model
estimates. Process knowledge concentrations are derived from historical tank sample data,
sample data from other tanks, waste transfers, and chemical additions.
Next, waste-type template concentrations are used when other information is not available. Solid
waste-type templates are based on sample data for a particular waste type supplemented with
process knowledge calculations and waste-type concentrations from the HDW model.
Liquid-waste-type templates are based on waste-type concentrations from the HDW model,
adjusted for process knowledge of mercury and other water-insoluble metals.
Lastly, HDW model-based estimates are used if the preceding information is unavailable for all
of the standard radionuclide constituents except for 137mBa, 228Ra, and 90Y which are calculated
from 137Cs, 232Th, and 90Sr, respectively. Model-based values for tank waste radionuclides are
derived from fuel irradiation and plant process records.
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4.2 BEST-BASIS INVENTORY UNCERTAINTY
Uncertainty in the BBI estimates consists of three components; uncertainty in the total inventory
summed over all of the waste tanks, uncertainty in the inventory estimate within each waste tank,
and uncertainty in the inventory estimate within each phase of each waste tank. Uncertainty in
the total inventory summed over all of the waste tanks affects the total inventory that will be
disposed of in separate waste form types at the IDF.
4.2.1 Total Best-Basis Inventory Uncertainty
Uncertainty in the total inventory in all of the waste tanks affects the total inventory that will be
disposed of in separate waste form types at the IDF. Estimating inventories using process
knowledge calculations involves consideration of reactor fuel irradiation and chemical
separations operations, as well as transfer and processing of tank contents. Incomplete
knowledge of the degree of irradiation, process extraction and separations efficiencies, plant
stream flow rates that affect recovery and distribution, and process losses to the environment all
contribute to the uncertainty in developing process knowledge inventory estimates.
Over time, changes in the total BBI inventory have occurred. Generally adjustments have been
made to remove some of the conservative assumptions used in previous estimates to account for
new information, or to align inventory estimates with tank sampling results. For example, some
of the significant uncertainties reported in HNF-3273, “Hanford Defined Waste Model
Limitations and Improvements” were addressed in Revision 5 of the HDW model, which forms
the basis for the 2014 BBI. Because the 2014 BBI represents the most current available
information, it is planned to be used for the 2017 IDF PA analysis.
In order to address global inventory uncertainty, it is recommended that the 2017 IDF PA
analysis perform a sensitivity study using the more conservative inventory estimates from either
the 2002 BBI or the 2014 BBI. The most significant differences between the two BBI estimates
are discussed in Section 4.3. For the sensitivity case, it is recommended that the HTWOS
partitioning fractions from 2017 IDF PA be applied to the 2002 BBI for each waste form that
will be disposed in the IDF. The allocation of inventory between waste forms for each HTWOS
run case is presented in Section 9.0.
4.2.2 Tank and Waste Phase Uncertainties
Uncertainty in the inventory within each waste tank and within each phase of each waste tank is
best characterized as representing the variability in the concentration of the constituents that will
be treated at the WTP. When feed to the WTP is staged in feed staging tanks that are not
completely emptied during a transfer to the WTP, feed blending occurs and the inventory
allocation to different waste tanks captured in the TWINS database becomes less significant to
the variability of the waste forms.
As the waste treatment mission progresses, the remaining feed becomes more blended resulting
in a more averaged feed composition near the end of the mission than may be experienced at the
beginning of the mission. This change in feed composition effectively results in a temporal
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variability that could result in early production feed compositions that are more or less
concentrated than the highly blended product that occurs later in the mission. This variation in
feed composition would result in variability of the concentration of constituents of potential
concern (COPCs) within the waste streams and waste forms destined for disposal at the IDF. For
a disposal facility that is filled by “lifts” stacked one above another, temporal variability would
manifest into spatial variability with early production waste forms being placed in the bottom
“lifts” and later production waste forms placed in the upper “lifts.” If early production waste
forms contain higher inventories of certain COPCs, then the later production waste forms placed
in the “lifts” above them will have lower concentrations of these same COPCs such that temporal
variability in the WTP feed composition would become less significant. Therefore, the average
inventories provided by the HTWOS process flowsheet model represent a reasonable approach
for the 2017 IDF PA analysis.
Allocation of the chemical and radionuclide inventory between different waste phases could also
affect the inventory variability for each waste form. To address this uncertainty, run cases were
developed to explore the effects that these different allocations would have on the different IDF
waste streams. The run cases developed for this purpose are discussed in Section 6.1 of this data
package.
4.3 BEST-BASIS INVENTORY COMPARISON
The BBI tank waste inventory estimates used in the TC&WM EIS were based on published data
from TWINS as of December 1, 2002. All radionuclides were decayed to January 1, 2001. Any
sample data that were released and waste transfers that occurred after December 1, 2002 were
not included (DOE/ORP-2003-02, Environmental Impact Statement for Retrieval, Treatment,
and Disposal of Tank Waste and Closure of Single-Shell Tanks at the Hanford Site, Richland
WA Inventory and Source Term Data Package).
The BBI is maintained through quarterly updates as new information about tank operations and
tank contents are processed. Although newer BBI estimates were available when the TC&WM
EIS modeling was performed, the TC&WM EIS team used the 2002 BBI for tank waste
inventory data based in part on the results of a 2005 review of the 2002 BBI estimates by the
Washington State Department of Ecology (Ecology) and several DOE offices (i.e., Office of
River Protection; Richland Operations Office; Office of Health, Safety, and Security; Office of
Environmental Management; and Office of the General Counsel), and also based in part on the
review of the 8-year span of BBI data and uncertainty (Appendix D, Section D.1.1.5 of the
TC&WM EIS).
The 2017 IDF PA will use the BBI estimate current in November 2014 as a starting point. In
lieu of re-running the HTWOS model to partition the tank inventory into different waste streams,
sensitivity analyses could assume that the starting inventory allocated to each waste stream is
proportional to the increase or decrease in the BBI inventories for each contaminant. For
instance, a sensitivity case using the BBI estimates from the TC&WM EIS could increase the
amount of iodine in each waste form by 39%. This increase would only be applicable to the
waste streams that originated as tank waste. Equitable distributions of the extra inventory may
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not be consistent with the processes that are used to treat the waste, but could give an indication
of the impact of the uncertainty in the BBI total inventory estimate. A separate sensitivity case
could also be performed using the same waste stream partitioning and volume estimates from
Run Case 7 (Section 6.1) with the inventory used in the TC&WM EIS.
The updated tank waste inventory estimates presented in this data package for WTP-generated
waste streams was published from TWINS as of November 2014 (RPP-33715, Rev. 9,
“Double-Shell and Single-Shell Tank Inventory Input to the Hanford Tank Waste Operations
Simulator Model – 2015-2 Update”). All radionuclides were decayed to January 1, 2008.
A comparison of the December 2002 and November 2014 BBI estimates (with radionuclides
decayed to January 1, 2008) is presented in Table 4-1.
A review of the changes in the BBI estimates over a 12-year period between December 2002 and
November 2014 presented in Table 4-2 shows the following:
All of the radionuclide estimates have decreased since the 2002 BBI estimate was
generated except for 241Am, 90Sr, and 233U, 234U, 235U, and 238U which have increased by
8 to 22%. The only long-lived radiological risk driver in this grouping is the uranium
isotope.
Only two chemical estimates, mercury and total uranium, have increased. All the other
chemical constituents have decreased by 1 to 21%.
The largest decrease in the radiological risk drivers was that of 129I, at 39%.
The largest increase in the radiological risk drivers was 233U, 234U, 235U, and 238U at 22%.
The largest increases in chemical hazard drivers were mercury at 9% and total uranium at
8%
99Tc and 129I values in the 2002 BBI are near the higher end of the range of values
reported between December 2002 and November 2014. Therefore, the 2002 BBI
estimate for these radionuclides represents some degree of conservatism.
Total uranium and uranium isotope values in the 2002 BBI are near the lower end of the
range of values reported between December 2002 and November 2014. The range of
values reported is smaller than the uncertainty itself.
Uranium (total) and uranium isotopes (233U, 234U, 235U, and 238U) are more highly retained in soil
and waste forms and less mobile in the environment, so their contribution to the long-term
impacts analysis should be smaller than the contribution from more mobile radionuclides
(i.e., 99Tc and 129I).
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Table 4-1. Best-Basis Inventory Comparison.
Column 1 EIS BBI
(December 2002 BBI
Decay Date:
January 1, 2008)1
Column 2 IDF BBI
(November 2014 BBI
Decay Date:
January 1, 2008)2
Percent Change
[(Column 2-
Column 1)/
Column 1]
Radionuclides Curies Curies Percent
Americium-241 1.45E+05 1.57E+05 +8
Carbon-14 3.12E+03 5.51E+02 -82
Cesium-137 3.90E+07 3.90E+07 0
Hydrogen-3 (tritium) 8.16E+03 2.82E+03 -65
Iodine-1293 4.82E+01 2.94E+01 -39
Neptunium-237 1.41E+02 1.15E+02 -18
Plutonium-239,-240 8.14E+04 6.02E+04 -26
Strontium-90 4.27E+07 4.76E+07 +11
Technetium-994 2.97E+04 2.65E+04 -11
Uranium-233,-234, -235,-238 9.38E+02 1.14E+03 +22
Chemicals Kilograms Kilograms Percent
Acetonitrile Not reported Not reported Not applicable
Benzene Not reported Not reported Not applicable
Butanol (n-butyl alcohol) Not reported Not reported Not applicable
Chromium 5.98E+05 5.91E+05 -1
Lead 8.41E+04 8.20E+04 -2
Mercury 1.83E+03 1.99E+03 +9
Nitrate 7.09E+07 5.60E+07 -21
Uranium (total) 5.97E+05 6.45E+05 +8
Polychlorinated biphenyls Not reported Not reported Not applicable
2,4,6-Trichlorophenol Not reported Not reported Not applicable
1 DOE/EIS-0391, “Final Tank Closure and Waste Management Environmental Impact Statement for the Hanford Site,
Richland, Washington,” Table D-8. 2 RPP-33715, Rev. 9, “Double-Shell and Single-Shell Tank Inventory Input to the Hanford Tank Waste Operations Simulator
Model-2015 – 2 Update.” 3 Inventory analysis presented by Nez Perce tribe at March 2015 scoping meeting concludes tank farm inventory for 129I is
estimated to be 34.1 Ci. Although this estimate is greater than the November 2014 BBI estimate of 29.4 Ci, it is bounded by
the DOE/EIS-0391 inventory of 48.2 Ci. 4 Inventory analysis presented by Nez Perce tribe at March 2015 scoping meeting concludes tank farm inventory for 99Tc is
estimated to be 28,563. Although this estimate is greater than the November 2014 BBI estimate of 26,500 Ci, it is bounded
by the DOE/EIS-0391 inventory of 29,700 Ci.
BBI = Best-Basis Inventory EIS = Environmental Impact Statement IDF = Integrated Disposal Facility
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Table 4-2. Hanford Tank Waste Historical Inventories for Technetium-99 and Iodine-129. (3 sheets)
Radionuclide Tank Inventory
(Ci)a Basis Source
Tc-99 2.72E+04
(3.43E+04)
ORIGEN2b calculation for single pass and N-reactor production (minus K basin fuels
and minus 20% Tc-99 loss from the waste stream that was sent offsite). WHC-SD-WM-RPT-164,
Rev. 0
I-129 6.62E+01 ORIGEN2b calculation for single pass and N-reactor production (minus K basis fuels).
Tc-99 3.26E+04 ORIGEN2b production and DKPRO separations processing no Tc-99 losses during
separations (Hanford Defined Waste [HDW] Model conservative). HNF-SD-WM-TI-740,
Rev. 0 I-129 6.30E+01
ORIGEN2b production and DKPRO separations processing no I-129 losses during
separations (HDW Model conservative).
Tc-99 3.21E+04 TRACc database adjusted to the 1994 Integrated Databased.
DOE/EIS-0189 I-129 3.83E+01 See Volume 2, Appendix A of DOE/EIS-0189.
Tc-99 4.70E+04 Limited double-shell tank analytical results, TRACc database, and HDW Rev. 1e
normalized to HNF-SD-WM-TI-740 (No Tc-99 losses during separations process). HNF-SD-WM-SP-012,
Rev. 0 I-129 N/A No I-129 losses during separations process.
Tc-99 2.83E+04 Best-Basis Inventory (BBI) as of October 1, 1998. HNF-SD-WM-SP-012,
Rev. 1 I-129 9.91E+01 BBI as of October 1, 1998.
Tc-99 2.89E+04 BBI as of October 1998. HNF-4921, Rev. 0
I-129 1.01E+02 BBI as of October 1998.
Tc-99 3.00E+04 BBI as of January 11, 2000. HNF-SD-WM-SP-012,
Rev. 2 I-129 6.29E+01 BBI as of January 11, 2000.
Tc-99 3.10E+04 BBI as of June 2001. HNF-SD-WM-SP-012,
Rev. 3 I-129 6.86E+01 BBI as of June 2001.
Tc-99 2.97E+04 BBI as of December 1, 2002. DOE/ORP-2003-02
I-129 4.82E+01 BBI as of December 1, 2002.
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Table 4-2. Hanford Tank Waste Historical Inventories for Technetium-99 and Iodine-129. (3 sheets)
Radionuclide Tank Inventory
(Ci)a Basis Source
Tc-99 2.88E+04 BBI as of June 2002. HNF-SD-WM-SP-012,
Rev. 4B I-129 4.88E+01 BBI as of June 2002.
Tc-99 2.91E+04 BBI as of October 2003. HNF-SD-WM-SP-012,
Rev. 5A I-129 4.74E+01 BBI as of October 2003.
Tc-99 2.51E+04
(3.43E+04) ORIGEN2 productionf included process losses of 23% with respect to HDW Rev. 4.
RPP-19822, Rev.0
I-129 3.18E+01
(4.94E+01)
ORIGEN2 productionf included process losses 23% with respect to HDW Rev. 4, and
reduction in fission product yield change of approximately 23%.
Tc-99 2.68E+04 BBI as of September 22, 2004. TWINS (2004)
I-129 4.39E+01 BBI as of September 22, 2004.
Tc-99 2.64E+04 BBI as of October 2010. DOE/EIS 0391
I-129 2.94E+01 BBI as of October 2010.
Tc-99 2.65E+04 BBI as of November 2014. RPP-33715, Rev. 9
I-129 2.94E+01 BBI as of November 2014.
a Numbers in brackets represent total reactor production. b Oak Ridge Isotope Generation and Depletion Code (ORIGEN2) software code used to estimated reactor production of radionuclides (ORNL/TM-7175,
“A User’s Manual for the ORIGEN2 Computer Code”). c Track Radioactive Constituents computer code (TRAC) (SD-WM-TI-057, “Preliminary Estimation of the Waste Inventories in Hanford Tanks Through
1980”). d Integrated Database for Hanford Waste tanks (Letter 9404636B R2, “Request for Office of Waste Management Integrated Data Base High-Level Waste Data
Information Update”). e HDW – Hanford Defined Waste Model Rev. 1 (LA-UR-96-3860, “Hanford Tank Chemical and Radionuclide Inventories: HDW Model Rev. 4”). f Production calculations (RPP-13489, “Activity of Fuel Batches Processed Through Hanford Separations Plants, 1944 Through 1989”).
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Table 4-2. Hanford Tank Waste Historical Inventories for Technetium-99 and Iodine-129. (3 sheets)
Radionuclide Tank Inventory
(Ci)a Basis Source
References:
DOE/EIS-0189, “Tank Waste Remediation System, Hanford Site, Richland, Washington, Final Environmental Impact Statement.”
DOE/EIS-0391, “Final Tank Closure and Waste Management Environmental Impact Statement for the Hanford Site, Richland, Washington.”
DOE/ORP-2003-02, Environmental Impact Statement for Retrieval, Treatment, and Disposal of Tank Waste and Closure of Single-Shell Tanks at the Hanford
Site, Richland WA Inventory and Source Term Data Package.
HNF-4921, “Immobilized Low-Activity Tank Waste Inventory Data Package.”
HNF-SD-WM-SP-012, Rev. 0, “Tank Waste Remediation System Operation and Utilization Plan.”
HNF-SD-WM-SP-012, Rev. 1, “Tank Waste Remediation System Operation and Utilization Plan.”
HNF-SD-WM-SP-012, Rev. 2, “Tank Farm Contractor Operation and Utilization Plan.”
HNF-SD-WM-SP-012, Rev. 3, “Tank Farm Contractor Operation and Utilization Plan.”
HNF-SD-WM-SP-012, Rev. 4B, “Tank Farm Contractor Operation and Utilization Plan.”
HNF-SD-WM-SP-012, Rev. 5A, “Tank Farm Contractor Operation and Utilization Plan.”
HNF-SD-WM-TI-740, “Standard Inventories of Chemicals and Radionuclides in Hanford Tank Wastes.”
RPP-19822, “Hanford Defined Waste Model – Revision 5.0.”
RPP-33715, “Double-Shell and Single-Shell Tank Inventory Input to the Hanford Tank Waste Operations Simulator Model – 2015-2 Update.”
Tank Waste Information Network System (TWINS), Queried 09/22/2004, [Best Basis Inventory, Best Basis Summary Report],
http://twins.pnl.gov:8001/twins.htm.
WHC-SD-WM-RPT-164, “Inventories for Low-Level Waste Tank Waste.”
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The differences noted in Table 4-2 are primarily due to the BBI Improvement Initiative4, which
was implemented after December 2002, and included the following:
Updated the Oak Ridge Isotope Generation and Depletion Code (ORIGEN2)
(ORNL/TM-7175, “A User’s Manual for the ORIGEN2 Computer Code”) fuel activity
estimates
Updated the HDW model to Revision 5, which accounted for a release of 3H (tritium), 14C, and 129I to the environment and shipment of offsite 99Tc with uranium (RPP-19822)
Updated the BBI templates with new sample data that added a second type of
Reduction-Oxidation (REDOX) Facility waste to the 241-SX Tank Farm, resulting in an
increase in 241-SX Tank Farm inventory
Eliminated non-credible sample detection limit values from inventory estimates
Incorporated new sample data, including 129I analysis of 241-BY Tank Farm salt cake.
4.4 TANK INVENTORY HISTORY OF TECHNETIUM-99 AND IODINE-129
Since mobile radionuclides such as 99Tc and 129I are the two major contaminants of concern
when considering the groundwater impacts related to the disposal of LLW and MLLW at the
IDF, it is important to understand the uncertainties of these estimates.
Figures 4-1 and 4-2 illustrate the trend in the 99Tc and 129I inventories as a function of the year in
which the inventory information was published. Because of the long half-life of 99Tc and 129I,
making decay corrections does not appreciably change the inventory estimates for comparison
purposes. The 2002 BBI estimates used in the TC&WM EIS and the 2014 BBI estimates used in
the 2017 IDF PA analysis are shown in red for comparison purposes.
4.4.1 Technetium-99 Tank Waste Inventory History
The 99Tc present in tank waste was produced as a fission product from uranium that was
irradiated in reactors and processed through separations to extract plutonium at the Hanford Site.
From 1944 to 1989, about 99,000 metric tons of uranium was processed in separations plants
across the Hanford Site (HNF-SD-WM-TI-740, “Standard Inventories of Chemicals and
Radionuclides in Hanford Site Tank Wastes”). As a result, reactor production records show that
approximately 32,600 to 34,000 Ci of 99Tc were produced during this time.
4 During fiscal year 2002, an internal management assessment was conducted to assess compliance with BBI
requirements and prioritize BBI improvements. Assessment results are reported in RPP-10365, “Best-Basis
Inventory Assessment Report.” In October 2001, a value engineering session was conducted to identify BBI
customer needs and prioritize improvements as part of this management assessment. Results of the value
engineering session are discussed in Appendix A of RPP-7625, “Guidelines for Updating Best-Basis Inventory.”
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Figure 4-1. Published Technetium Inventories in Hanford Tank Waste (Section 4.4.1).
Figure 4-2. Published Iodine-129 Inventories in Hanford Tank Waste (Section 4.4.2).
2.97E+042.65E+04
0
5,000
10,000
15,000
20,000
25,000
30,000
35,000
40,000
45,000
50,000
1990 1995 2000 2005 2010 2015
Tc-99 Inventory
Cu
ries
4.82E+01
2.94E+01
0
20
40
60
80
100
120
1990 1995 2000 2005 2010 2015
I-129 Inventory
Cu
rie
s
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Table 4-2 provides historical inventory estimates showing the evolution of the inventory
estimates for 99Tc and 129I (RPP-20692, Rev. 1, “Inventory Data Package for the 2005 Integrated
Disposal Facility Performance Assessment”).
Although a single source of inventory does not exist for the entire operational period,
approximately 1,300 fuel batch records are available that document the amounts and types of
fuel processed, reactor burn-ups, dates irradiated fuel was removed from the reactor, cooling
times before separation, and dates of reprocessing to remove the plutonium. Additionally, waste
discharges to ponds, cribs and trenches were reasonably well documented.
Utilizing these 1,300 fuel batch records, the ORIGEN2 code (ORNL/TM-7175) estimates that
34,000 Ci of 99Tc were produced and that 27,400 Ci of 99Tc remain in Hanford waste tanks. This
early estimate excludes approximately 20% of the 99Tc that was produced in the reactors because
it was shipped offsite with the recovered uranium and was not sent to the Hanford waste tanks
(HNF-SD-WM-TI-740).
Subsequently, the ORIGEN2 code coupled with the decay (DK) and processing (PRO) computer
code (DKPRO), provides an estimate of 32,600 Ci of 99Tc in Hanford waste tanks. The DKPRO
code was developed at Hanford to generate output files listing the curie values for 99Tc and other
key radionuclides associated with each batch of irradiated fuel processed through the various
reprocessing steps assuming no losses during separations; the estimate is therefore considered to
be conservative.
As shown in Table 4-2, the one high estimate of 47,000 Ci was based on limited DST sample
data and early versions of the HDW model (HDW version 1) which did not allow any loss of 99Tc to waste streams not sent to tanks. The remaining estimates fall in the ranges of 26,500 to
34,000 Ci due to the evolution of reactor production calculations used by the ORIGEN2 software
code. Additionally, estimates for process losses have also been incorporated including
approximately 20% of the 99Tc produced in the reactors that was shipped offsite with the
recovered uranium (HNF-SD-WM-TI-740, RPP-19822).
Table 4-2, extracted from RPP-20692, Rev. 0, lists early to present total inventory estimates in
the Hanford waste tanks. Figure 4-1, also extracted from RPP-20692, Rev. 0, shows a slight
reduction in the 99Tc total inventory over time, which is likely due to a combination of the
availability of more sample data and refinements to the HDW model that estimates the fate of 99Tc in the production/reprocessing chemistry.
Efforts to refine the methodology and computer codes for predicting inventories in the waste
tanks at Hanford has continued. By 1999, a suite of computer codes that collectively produced a
BBI estimate for tank waste volumes, tank waste phases (supernate, salt cake, and sludge), and
tank waste tank inventories (curies for radionuclides and kilograms for chemicals) was adopted.
The BBI is the current official estimate of the waste tank inventories (46 radionuclides and
25 chemicals) in the SSTs and DSTs at the Hanford Site (HNF-SD-WM-TI-740).
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4.4.2 Iodine-129 Tank Waste Inventory History
The 129I present in Hanford waste tanks was also formed from the fission of uranium in nuclear
reactors. The estimates for the total 129I produced are based on reactor production calculations
and range between 49.4 and 66 Ci, neglecting any losses from the separations plants. Most of
the difference in these two estimates is based on a recent reduction in the 129I fission product
yield5 by approximately 23% and modeling of process losses (RPP-19822).
The corresponding BBI estimate for 129I based on measurement data has ranged between 29.4
and 101 Ci. The earlier BBI estimates for 129I tend to be higher than the production estimates
and the most current estimates because the earlier BBI was based on older versions of the HDW
model that did not include the most recent estimates of process losses, the elimination of
non-credible sample detection limit values, and the incorporation of new sample data including 129I analysis of 241-BY Tank Farm saltcake. As seen in Figure 4-2, 129I inventory has
demonstrated a high degree of variability over time.
Understanding the uncertainty of the 129I inventory to be disposed of at the IDF is important
because of its potential impact to groundwater. The TC&WM EIS analysis used the
December 2002 BBI estimate for 129I of 48.2 Ci and assumed that 80% goes to off-gas
(WT-ST-042, Rev. 10, “Curie Distribution for Alternatives 1, 2A, 2B, 3A, 3B, 3C, 4, 5, 6A, 6B,
and 6C”) which was disposed of at the IDF as a grouted MLLW.
The current BBI estimate for 129I is 29.4 Ci, which is reasonably consistent with ORIGEN2
production calculations documented in RPP-19822. Revisions to the 129I inventory in the BBI
database based on HDW Rev. 5 changes were not incorporated until October 2005 and have
changed very little since that time.
5 Yield refers to the fraction of a fission product produced per fission. Yield can be broken down by individual
isotope, chemical element spanning several isotopes of different mass number but same atomic number, or nuclei
of a given mass number regardless of atomic number.
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5.0 HANFORD TANK WASTE OPERATIONS SIMULATOR
HTWOS is a dynamic event simulation model and is commonly used at the Hanford Site to
estimate inventories in the WTP process flowsheet (RPP-17152, Rev. 12). In this data package,
HTWOS was used for developing inventory estimates for WTP waste streams that are planned to
be disposed of at the IDF such as:
ILAW glass
LAW melters
WTP SSW (debris and non-debris) and,
ETF-generated SSW.
The HTWOS model was used to partition the total inventory into these different waste streams.
Multiple model runs were performed to develop waste stream inventory estimates that account
for uncertainties in the performance of the treatment processes as well as uncertainties in the
WTP treatment process itself.
5.1 HANFORD TANK WASTE OPERATIONS SIMULATOR BACKGROUND
The HTWOS model uses the BBI, the tank farm operations processes that will be used to retrieve
and transfer the waste from the tanks, the WTP processes that will be used to separate the waste
into high-level and low-activity fractions, and the processes that will be used to generate the final
waste form(s).
To date, numerous scenarios for the fate of current tank waste have been produced that model
waste movement from Hanford’s SSTs and DSTs to its final disposition including IHLW glass,
ILAW glass, bulk vitrification, supplemental LAW, contact-handled and remote-handled TRU
waste, tank retrieval losses, tank residuals, and all secondary waste streams. The current process
flow evaluated by HTWOS is illustrated in Figure 5-1.
5.2 HANFORD TANK WASTE OPERATIONS SIMULATOR UNCERTAINTY AND
LIMITATIONS
Although HTWOS provides a “mass balance” of the inventory for each waste stream in the WTP
process flowsheet, these inventory mass balance estimates are highly dependent on projections of
process performance associated with the numerous processes including waste retrieval from
tanks, waste partitioning during pretreatment, and waste form generation. Many of the processes
are still undergoing development and are largely uncertain. These process uncertainties, along
with the uncertainties associated with tank waste compositions (BBI), are important
considerations when evaluating the distribution of contaminants in the IDF waste forms
generated by the HTWOS model.
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Figure 5-1. Hanford Tank Waste Operations Simulator Flow Sheet.
(LAWPS is not shown, however its paths are similar to WTP PT, except there is recycle from off-gas back to tanks).
ETF = Effluent Treatment Facility SALDS = State-Approved Land Disposal Site
HOG = High-Level Waste Off-Gas SLOG = Supplemental Low-Activity Waste Off-Gas
HTWOS = Hanford Tank Waste Operations Simulator STACK = Off-Gas to atmosphere
IDF = Integrated Disposal Facility TRU = transuranic
LAWPS = Low-Activity Waste Pretreatment System WTP = Waste Treatment and Immobilization Plant
LOG = Low-Activity Waste Off-Gas
In order to maintain mass balance at the end of the WTP mission, the HTWOS model tracks and
reports “Total Accumulation,” an inventory term which represents residual inventory left in
various vessels and HTWOS model logic blocks at the end of the model run. For analysis
Underground Tank
TRU Waste
Waste Treatment and Immobilization Plant
Pretreatment (PT)
High-level
Waste (HLW) Low-Activity
Waste (LAW)
Supplemental
Low-Activity
Waste (SLAW)
HLW
Canister
Spent/Failed
HLW Melter
Off-gas (HOG, LOG, SLOG)
LAW
Container
Spent LAW
Melter
Spent SLAW
Melter
Secondary
Solid Waste
(SSW)
STACK
ETF ETF-
Generated
SSW
SALDS
242-A Evaporator
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purposes, the “Total Accumulation” residual inventory was included as part of the 2017 IDF PA
inventory for both IDF and non-IDF waste streams. Excluding the tank farm and TRU residual
inventories, the remaining “Total Accumulation” inventory was manually allocated to ILAW
glass, LAW melters, WTP SSW, ETF generated SSW, and non-IDF waste streams using the
same partition fractions designated by HTWOS for each run case. The resulting adjusted
inventory for each IDF waste stream with radionuclides decayed to January 1, 2008 and
January 1, 2051 is included in Appendix A.
An understanding of the limitations as well as the inventory tracking and reporting features of
HTWOS relative to WTP SSW and ETF-generated SSW inventory projections is important when
evaluating the distribution of contaminants generated by the HTWOS model.
Simulating a series of events and activities the size and complexity of the WTP process requires
the use of numerous modeling simplifications, assumptions, and operating paradigms. Each of
these introduce elements of uncertainty within the overall HTWOS operations. Areas of
uncertainty include waste phase partitioning fractions, distribution of the key radionuclides and
chemicals, operational decisions, and overall flowsheet configuration. These uncertainties, in
conjunction with the tank inventory uncertainties, are important considerations when evaluating
the result and behavior metrics generated by the HTWOS model.
When the HTWOS model was developed, its main purpose was to provide:
DST space projections
Overall mission metrics such as SST retrieval dates and waste immobilization completion
dates to meet certain legal milestones
Projections on the amount of immobilized waste produced at the end of the WTP
mission.
Waste chemistry and unit operations that directly impact these main purposes are modeled with
as much rigor as is practical. Waste chemistry and unit operations that only tangentially impact
these main purposes, such as WTP SSW and ETF-generated SSW compositions needed to
support the 2017 IDF PA, have received significantly less attention.
Although improvements to the HTWOS modeling of SSW has been discussed, such
improvements have not been implemented for the following reasons:
Not enough information exists to develop meaningful assumptions for estimating how
much of the tank waste would be captured in the SSW stream, such as failed equipment
(excluding failed melters) and discarded personnel protective equipment
Inventory expected in the SSW stream was considered to be substantially less than the
tank waste content of other streams sent to the IDF
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The contents of the SSW would likely be drawn from other waste streams disposed in the
IDF and the waste content of these other streams was considered to include or bound the
waste content of the SSW streams.
The projection of ETF-generated SSW inventory was considered to be a sufficient level of detail
for the HTWOS model when the model was developed.
In consideration of these uncertainties and limitations, HTWOS was used for developing the IDF
waste form inventory estimates in the TC&WM EIS analysis and was also used to develop the
2017 IDF PA waste form inventory estimates presented in this data package. Sensitivity cases
are planned to be included as necessary to explore the range uncertainties associated with
HTWOS limitations.
5.3 HANFORD TANK WASTE OPERATIONS SIMULATOR COMPARISON
As previously mentioned, the HTWOS model uses a “mass balance” approach that relies on
waste stream partitioning fractions to model the flows of material through the WTP systems.
The processes and assumptions behind the current HTWOS model (October 2014) are
documented in HTWOS Version 8.1 (RPP-17152, Rev. 12). The processes and assumptions
(and consequently the waste stream partitioning fractions) have changed over time as the details
of the WTP design have evolved. Since the WTP design is not fully complete, there is an
element of uncertainty in the waste stream partitioning fractions and the distribution of key
radionuclides and chemicals among the various waste forms which are sensitive to these
uncertainties.
To qualitatively characterize uncertainty, Table 5-1 has been prepared showing the distribution
of key constituents among the glass and non-glass waste forms. The columns labeled “TC&WM
EIS HTWOS” show the distribution of key constituents and the partitioning fractions from the
TC&WM EIS Tank Closure Alternative 2A. The columns labeled “2017 IDF PA HTWOS”
show the distribution of key constituents and the partitioning fractions from Run Case 7
(Section 6.0) which is most representative of the current WTP process flow sheet as of
October 2014.
The changes in the distribution of 129I between glass and non-glass waste forms are important in
understanding factors that may influence calculated impacts. The current WTP process
flowsheet model retains much more 129I in ILAW glass than the TC&WM EIS, with nearly all
the remainder going to WTP SSW. In the TC&WM EIS case, most of the 129I inventory not
retained in ILAW glass was found in ETF-generated SSW, followed by WTP SSW.
Furthermore, Chapter 7 of the TC&WM EIS showed that the risk budget for 129I at the IDF fence
line was strongly influenced by the distribution of 129I between glass and non-glass waste forms.
In terms of impacts from chemicals, the decrease in the inventory of nitrate for ETF-generated
SSW as shown in Table 5-1 for the “2017 IDF PA HTWOS” will have a similar effect on the
calculated impacts at the IDF fence line.
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Table 5-1. Comparison of Hanford Tank Waste Operations Simulator Partitioning Fractions from the Tank Closure and
Waste Management Environmental Impact Statement versus Current Hanford Tank Waste Operations Simulator
Partitioning Fractions.
Key
Contaminant
ILAW Glass LAW Melter WTP Secondary Solid
Waste
ETF-Generated
Secondary Solid Waste Total Inventory to IDF
TC&WM
EIS
HTWOS
2017 IDF
PA
HTWOS
TC&WM EIS
HTWOS
2017 IDF
PA
HTWOS
TC&WM
EIS
HTWOS
2017 IDF
PA
HTWOS
TC&WM
EIS
HTWOS
2017 IDF
PA
HTWOS
TC&WM
EIS
HTWOS
2017 IDF
PA
HTWOS
I-129 19.8%
(9.56)
56.2%
(16.5)
Included as part
of ILAW glass
0.08%
(<1)
9.7%
(4.65)
41.2%
(12.1)
69.7%
(33.6)
0.22%
(<1) 47.8 28.6
Tc-99 96.9%
(28,800)
99.6%
(26,400)
Included as part
of ILAW glass
0.14%
(37.5)
1.5%
(431)
0.08%
(20.0)
0.3%
(86.3)
0.0%
(<1) 29,300 26,500
U isotopes 5.8%
(54.7)
1.4%
(15.8)
Included as part
of ILAW glass
0.0%
(<1)
0.4%
(3.64)
0.0%
(<1)
0.0%
(<1)
0.0%
(<1) 58.4 15.8
Cr 76.2%
(456,000)
83%
(490,000)
Included as part
of ILAW glass
0.13%
(744)
0.3%
(1,940)
0.13%
(743)
<1%
(44.3)
<1%
(4.30) 458,000 491,000
Utotal 6.3%
(37,400)
1.3%
(8,100)
Included as part
of ILAW glass
<1%
(11.5)
0.4%
(2,320)
0.0%
(<1)
<1%
(40.0)
<1%
(8.30) 39,800 8,120
NO3 0.0%
(0)
0.0%
(0)
Included as part
of ILAW glass
0.0%
(0)
0.0%
(<1)
0.0%
(0)
12.7%
(9,010,000)
0.29%
164,000 9,010,000 164,000
Note: Radionuclides are reported in (curies) and chemicals reported in (kilograms) and expressed as percentages of the 2002 or 2014 Best-Basis Inventory as applicable. Note
that these IDF inventories include only waste streams that are disposed of at the IDF and therefore do not represent perfect mass balance. Differences can be attributed to
destruction during treatment, stack losses, and disposal offsite at a geologic repository. The TC&WM EIS reports nitrate values calculated as nitrate plus nitrite (oxidized).
EIS = Environmental Impact Statement IDF = Integrated Disposal Facility PA = Performance Assessment
ETF = Effluent Treatment Facility ILAW = Immobilized Low-Activity Waste TC&WM = Tank Closure and Waste Management
HTWOS = Hanford Tank Waste Operations Simulator LAW = Low-Activity Waste WTP = Waste Treatment and Immobilization Plant
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Many of the differences presented in Table 5-1 are due to treatment destruction assumptions
applied to the LAW melter and off-gas systems (i.e., NO3) and the handling of recycle streams
that lead to the use of different split fractions for certain process streams. The earlier HTWOS
model that was used in the TC&WM EIS had a simple recycle scheme for the LAW melter
off-gas (see Figure D-8 in RPP-17152, Rev. 1), whereas the more recent model recycles liquid
effluents to more locations for more effective management of the effluents (see Figure C-15 in
RPP-17152, Rev. 12). Additionally, for the TC&WM EIS analysis, the nitrite inventory in the
tanks was converted on a molecular-weight basis and added to the nitrate inventory and reported
as nitrate.
Table 5-1 shows important differences between the “TC&WM EIS HTWOS” and the “2017 IDF
PA HTWOS” inventory distributions for key mobile radionuclides (99Tc and 129I) in ILAW glass
versus non-glass waste forms (WTP SSW plus ETF-generated SSW). The source of these
differences is largely attributed to changes in the BBI estimates and updates to the HTWOS
partitioning assumptions associated with these constituents.
The 2002 BBI estimate for 99Tc used in the TC&WM EIS was 29,700 Ci, whereas the
November 2014 BBI estimate being used in the 2017 IDF PA is 26,500 Ci, a decrease of
approximately 11% (Table 4-1). The most notable difference between the TC&WM EIS and
2017 PA analysis with respect to 99Tc is the amount that reports to non-glass waste forms (WTP
SSW plus ETF-generated SSW). The TC&WM EIS reports a combined total of 517.3 Ci for
these waste forms, whereas the 2017 IDF PA reports a combined total of only 20 Ci, a significant
decrease of approximately 96%.
A simple comparison can be made by applying the partitioning fractions used in the TC&WM
EIS for Tank Closure Alternative 2A to the 2014 BBI estimates for 99Tc from the 2017 IDF PA
to illustrate how these waste form inventories would look if they were developed using the same
partitioning fractions used in the TC&WM EIS (Figure 5-2).
As shown, the total curies of 99Tc reporting to non-glass waste forms for the 2017 IDF PA
analysis is 478 Ci, which is within 11% of the TC&WM EIS analysis, demonstrating the impact
that relatively small changes in partitioning fractions (< 2%) have on the fate of 99Tc in tank
waste processed at WTP.
Additionally, the 2002 BBI estimate for 129I that was used in the TC&WM EIS was 48.2 Ci
whereas the November 2014 BBI estimate being used in the 2017 IDF PA is 29.4 Ci, a decrease
of approximately 39% (Table 4-2). The ILAW glass partitioning factor for 129I used in the
TC&WM EIS was approximately 20% based on DOE Office of River Protection guidance
(Appendix E of the TC&WM EIS), whereas the 2017 IDF PA used a partitioning factor of 56%
based on refinements to the LAW melter decontamination factors for volatile constituents
(24590-WTP-RPT-PT-02-005, Rev. 7). As a consequence of capturing much less 129I in ILAW
glass, the TC&WM EIS reports a combined total of 38.25 Ci to non-glass waste forms (WTP
SSW plus ETF-generated SSW), whereas the PA reports a combined total of only 12.1 Ci to
non-glass waste forms, a significant decrease of approximately 68%.
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Figure 5-2. Technetium-99 Comparison using Tank Closure and Waste Management
Environmental Impact Statement Partitioning Fractions.
BBI = Best-Basis Inventory ILAW = Immobilized Low-Activity Waste
EIS = Environmental Impact Statement PA = Performance Assessment
ETF = Effluent Treatment Facility TC&WM = Tank Closure and Waste Management
IDF = Integrated Disposal Facility
A simple comparison can be made by applying the partitioning fractions used in the TC&WM
EIS for Tank Closure Alternative 2A to the 2014 BBI estimates for 129I from the 2017 IDF PA to
illustrate how these waste stream inventories would look if they were developed using the same
partitioning fractions used in the TC&WM EIS (Figure 5-3).
Although the partitioning fractions are the same, the inventory of 129I in non-glass waste forms
being analyzed in the 2017 IDF PA is still significantly less (~40%) than what was analyzed in
the TC&WM EIS, demonstrating the influence that changes to the BBI estimates (2002 versus
2014) have relative to analysis of 129I.
28,800
86.3
431
29,317
25,679
79.5
398
26,156
1
10
100
1,000
10,000
100,000
ILAW glass ETF GeneratedSecondary Solid
Waste
Secondary SolidWaste
Total
Tc-99 Inventories Using 2014 BBI and TC&WM EIS Partitioning Factors
EIS
2017 IDF PA
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Figure 5-3. Iodine-129 Comparison.
BBI = Best-Basis Inventory ILAW = Immobilized Low-Activity Waste
EIS = Environmental Impact Statement PA = Performance Assessment
ETF = Effluent Treatment Facility TC&WM = Tank Closure and Waste Management
IDF = Integrated Disposal Facility
9.56
33.6
4.65
47.81
5.82
20.5
2.85
29.16
1
10
100
ILAW glass ETF GeneratedSecondary Solid
Waste
Secondary SolidWaste
Total
I-129 Inventories Using 2014 BBI and TC&WM EIS Partitioning Factors
EIS
2017 IDF PA
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6.0 WASTE TREATMENT AND IMMOBILIZATION PLANT GENERATED WASTE
INVENTORY ESTIMATES—RESULTS
Five HTWOS model run cases (Run Cases 7, 8B, 9, 10A, and 10B)6 were developed to explore
the inventory estimates for waste streams going to the IDF that result from processing tank waste
through the WTP Facility using different process flowsheet assumptions. These assumptions
were developed to evaluate a range of retention efficiencies relative to 99Tc and 129I in ILAW
glass, since the WTP process flowsheet is in flux given ongoing technical decisions and
regulatory discussions. The first three of the five HTWOS model runs that were performed
(Cases 7, 8B, and 9) address operational uncertainties (i.e., technetium removal and WTP
without Low-Activity Waste Pretreatment System (LAWPS). The other two cases evaluate
operational uncertainties regarding process stream recycle efficiencies. The process flowsheet
for the TC&WM EIS Case (Tank Closure Alternative 2B without 99Tc removal) is also included
for comparison purposes; this case is referred to as Case 1.
Summary tables for each HTWOS run case showing the distributions of key radionuclides and
chemicals for each IDF waste stream are provided in Section 9.0. Summary tables for the
TC&WM EIS run case provided for comparison purposes. These summary tables include a
limited number of contaminants and are included for convenience to facilitate comparisons
between the 2017 IDF PA and the results presented in Appendix D of the TC&WM EIS. For the
2017 IDF PA, complete inventory tables including all BBI constituents for the WTP waste
streams are provided in Appendix A of this data package.
A LAWPS facility is included in all process flowsheets with the exception of Case 9. LAWPS,
as analyzed here, allows waste to be treated earlier in time but has no real impact on inventory
since all tank waste inventory will be processed through WTP regardless of the timeframe.
Additionally, the different process flowsheet scenarios presented here demonstrate stream
recycle and glass retention efficiency alternatives that will impact the partitioning of
radionuclides and hazardous chemicals into different secondary waste streams which influence
the contaminant loadings in non-glass waste forms planned for disposal at the IDF.
6.1 THE ENVIRONMENTAL IMPACT STATEMENT AND HANFORD TANK
WASTE OPERATIONS SIMULATOR CASES INVENTORY ESTIMATES
Case 1 – The TC&WM EIS Case
In accordance with 78 FR 75913, DOE has not selected a supplemental treatment technology at
this time, and has implemented Tank Closure Alternative 2B, without supplemental treatment
and WTP without 99Tc removal in the WTP Pretreatment Facility. For the purpose of this data
package, implementation of the Record of Decision is equivalent to the TC&WM EIS
Alternative 2A inventory.
6 Run Cases 2 through 6 were not used for the PA analysis because they were either experimental or because they
were not consistent with 78 FR 75913.
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The process flowsheet for the TC&WM EIS Case is presented in Figure 6-1. The inventory
summary table for the IDF waste streams from the TC&WM EIS Case is presented in
Section 9.0.
Figure 6-1. Tank Closure Alternative 2B Flowsheet from the Tank Closure and Waste
Management Environmental Impact Statement.
Adapted from Figure D-3 (without Tc-99 removal) from Appendix D of DOE/EIS-0391, “Final Tank Closure and Waste
Management Environmental Impact Statement for the Hanford Site, Richland, Washington”
HLW = High-Level Waste ILAW = Immobilized Low-Activity Waste
IDF = Integrated Disposal Facility LAW = Low-Activity Waste
Case 7 – Current Operations Case
The first HTWOS run case was designed to represent the WTP process flowsheet as of
October 2014 using the most current operational assumptions which are in flux, given technical
decisions and regulatory discussions. This case is designated as Case 7, the Current Operations
Case.
The key process flowsheet assumptions for Case 7 include the following:
WTP startup includes 10 years of LAWPS operations to accelerate the pretreatment of
LAW and the use of the LAW melter until the WTP Pretreatment Facility is operational
and the WTP equivalent is operating.
No 99Tc removal in pretreatment (same as TC&WM EIS Alternative 2A).
During the time that LAWPS is operational, the Submerged Bed Scrubber (SBS), Wet
Electrostatic Precipitator (WESP), and Caustic Scrubber (CS) off-gas streams would be
recycled back to tank farms. When WTP becomes operational (10 years later), the SBS
and WESP condensates would be recycled back to the Pretreatment Facility while the CS
waste stream would go to LERF/ETF. This represents the LAW flowsheet as of
October 2014 (ORP-11242, Rev. 7, “River Protection Project System Plan”).
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The primary waste product would be ILAW glass containers (same as TC&WM EIS
Alternative 2A).
During each pass, approximately 32% of the 99Tc is retained in the ILAW glass product.
The remainder goes into the off-gas system (SBS and WESP). The SBS and WESP
condensates are recycled back to the Pretreatment Facility. As a result of this recycle, the 99Tc retention of ILAW glass product is approximately 99% of the total 99Tc inventory,
which is similar to TC&WM EIS Alternative 2A. This case demonstrates the impacts of
a high-efficiency retention of 99Tc in glass due to recycle.
During each pass, approximately 20% of the 129I would be retained in the ILAW glass.
The remainder goes into the off-gas system (SBS and WESP). The SBS and WESP
condensates are recycled back to the Pretreatment Facility. As a result of this recycle, the 129I retention of ILAW glass product is 56%, which is much higher than was analyzed in
TC&WM EIS Alternative 2A (20%). Most of the 129I that is not retained in the glass
after recycle is captured in the carbon absorber media, which is disposed of at the IDF as
WTP SSW.
The process flowsheet for Case 7 is presented in Figure 6-2. The inventory summary table for
the IDF waste streams from Case 7 is presented in Section 9.0. The complete material balance
for Case 7 is included in Excel®7 spreadsheet SVF-4092, “IDF PA Case 7 - Current Information
Case - Mass Balance, MMR-50049.”
Figure 6-2. Case 7 – Current Information Case Flowsheet.
HLW = High-Level Waste LAW = Low-Activity Waste
IDF = Integrated Disposal Facility LAWPS = Low-Activity Waste Pretreatment System
ILAW = Immobilized Low-Activity Waste WTP PT = Waste Treatment and Immobilization Plant Pretreatment
7 Excel® is a registered trademark of Microsoft Corporation in the U.S. and other countries.
7
Tank WTP PT
8 LAW Melters
OffgasCleanup
2 HLW Melters
OffgasCleanup
LAWPS
ILAW glass to IDF
Secondary Waste to IDF
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The other four sensitivity cases (Run Cases 8B, 9, 10A, and 10B) were generated from Case 7
using slightly different process flowsheet assumptions.
Case 8B – Tc-99 Removal from LAW Vitrification Off-Gas Condensate
The key change to the Case 7 process flowsheet assumption for Case 8B includes:
99% removal of 99Tc from the LAW off-gas stream.
Note that the “Accumulator” term presented in this run case is not a WTP unit operation; rather,
it is a way for HTWOS to represent the total inventory being removed to demonstrate the
efficiency of removing 99Tc from SBS-WESP liquid off-gas stream which is in the pertechnetate
form. The disposition of the 99Tc in the “Accumulator” would be IHLW and offsite disposal, not
at the IDF.
The process flowsheet for Case 8B is presented in Figure 6-3. The inventory summary table for
the IDF waste streams from Case 8B is presented in Section 9.0. The complete material balance
for Case 8B is included in Excel® spreadsheet SVF-4094, “IDF PA Case 8B – Tc_Tc-99
Removal from LAW Vitrification Off-Gas Condensate - Mass Balance, MMR-50051.”
Figure 6-3. Case 8B – Technetium-99 Removal from Low-Activity Waste Vitrification
Off-Gas Condensate Flowsheet.
HLW = High-Level Waste LAWPS = Low-Activity Waste Pretreatment System
IDF = Integrated Disposal Facility SBS = Submerged Bed Scrubber
ILAW = Immobilized Low-Activity Waste WESP = Wet Electrostatic Precipitator
LAW = Low-Activity Waste WTP PT = Waste Treatment and Immobilization Plant Pretreatment
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Case 9 – Removal of LAWPS
The key changes to the Case 7 process flowsheet assumption for Case 9 include the following:
LAWPS would not be used. Operations would not start until the WTP Pretreatment and
HLW Facilities are completely ready.
This process flowsheet is somewhat representative of the TC&WM EIS process
flowsheet; however, the TC&WM EIS results are based on a different version of the BBI
(BBI 2002) and different partitioning assumptions for 129I, 99Tc, and other constituents.
The process flowsheet for Case 9 is presented in Figure 6-4. The inventory summary table for
the IDF waste streams from Case 9 is presented in Section 9.0 The complete material balance
for Case 9 is included in Excel® spreadsheet SVF-4095, “IDF PA Case 9 - Removal of LAWPS -
Mass Balance, MMR-50052.”
Figure 6-4. Case 9 – Removal of Low-Activity Waste Pretreatment System Flowsheet.
HLW = High-Level Waste ILAW = Immobilized Low-Activity Waste
IDF = Integrated Disposal Facility LAW = Low-Activity Waste
Case 10A – 32% 99Tc Retention in ILAW Glass
Case 10A represents a contrived scenario that limits the amount of the LAW off-gas stream that
is recycled back into the melters. This unanticipated operating scenario was developed as a
sensitivity case and does not represent a realistic WTP operating condition given the current
configuration of the facilities. This case was contrived to increase the amount of key
contaminants such as 99Tc in non-glass waste forms in order to evaluate its impact on the IDF
system. In the typical operating configuration, the off-gas condensate would be routed to the
ETF for treatment. In order to determine the limitations of the IDF system, the off-gas stream
routed to the ETF in this sensitivity case is done with the realization that it does not meet the
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current ETF waste acceptance criteria. The key change to the Case 7 process flowsheet
assumption for Case 10A includes:
32% of the 99Tc would be retained in the glass product, to investigate the disposal
impacts associated with reduced retention of 99Tc in ILAW glass.
DM-10 testing at Vitreous State Laboratory (VSL) showed that the lowest 99mTc retention in
LAW glass averaged across all LAW feed types tested was 32% (RPP-54130, “Technetium
Retention in WTP LAW Glass with Recycle Flow-Sheet: DM10 Melter Testing,
VSL-12R2640-1, Rev. 0,” Table 5.9). This low retention efficiency represents a sensitivity case
and is not the actual 99Tc ILAW glass retention rate that is expected during WTP operations.
The purpose of this case is to allow the PA team to test the IDF system and explore the impacts
of 99Tc captured in a grouted secondary waste form rather than in a glass waste form.
The process flowsheet for Case 10A is presented in Figure 6-5. The reduced efficiency in the
off-gas recycle was implemented in HTWOS by eliminating the recycle stream from the model.
As a result, the only exit for 99Tc from the process flowsheet was through the off-gas condensate.
The result is that much more material ends up on the media used to treat the off-gas or at the
LERF/ETF. Because this run case was configured to exclude recycle, the glass volume produced
is consistent with a single-pass operation and not a reduced efficiency recycle loop. The
inventory summary table for the IDF waste streams from Case 10A is presented in Section 9.0.
The complete material balance for Case 10A is included in Excel® spreadsheet SVF-4096, “IDF
PA Case 10A - Single Pass Tc_Tc-99 Retention in ILAW Glass of 32% - Mass Balance,
MMR-50053.”
Figure 6-5. Case 10A and 10B – Low and Medium Efficiency Recycle.
HLW = High-Level Waste LAW = Low-Activity Waste
IDF = Integrated Disposal Facility LAWPS = Low-Activity Waste Pretreatment System
ILAW = Immobilized Low-Activity Waste WTP PT = Waste Treatment and Immobilization Plant Pretreatment
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Case 10B –68% 99Tc Retention in ILAW Glass
The key change to the Case 10A process flowsheet assumption for Case 10B includes:
68% of the 99Tc would be retained in the glass product, to investigate the disposal
impacts associated with reduced retention of 99Tc in ILAW glass.
DM-10 testing at VSL demonstrated 99mTc retention in LAW glass averaged across all LAW
feed types tested was 68% with recycle (RPP-54130, Table 5.9). This retention efficiency
represents a contrived sensitivity case and is not the actual 99Tc ILAW glass retention rate
expected during WTP operations. The purpose of this case is to allow the PA team to understand
the IDF system behavior in response to perturbations and explore the impacts of 99Tc captured in
a grouted secondary waste form rather than in a glass waste form. This sensitivity case is done
with the realization that this liquid off-gas waste stream does not meet the current ETF waste
acceptance criteria.
The process flowsheet for Case 10B is presented in Figure 6-5. The inventory summary table for
the IDF waste streams from Case 10B is presented in Section 9.0. The complete material
balance for Case 10B is included in Excel® spreadsheet SVF-4097, “IDF PA Case 10B - Recycle
Pass Tc_Tc-99 Retention in ILAW Glass of 68% - Mass Balance, MMR-50054.”
Note that a subsequent analysis at VSL as presented in report VSL-13R2800-1, “Wet
Electrostatic Precipitator Performance and Technetium-Rhenium Behavior in LAW Recycle
Flow-Sheet” indicates that previously measured technetium concentrations in glass samples are
biased low by approximately 8%. However, the range of 99Tc retention in ILAW glass being
investigated in Run Cases 7 through 9 and in sensitivity cases 10A and 10B is approximately
32% to 99%, which is broad enough to include this new information.
6.2 WASTE TREATMENT AND IMMOBILIZATION PLANT SECONDARY SOLID
WASTE STREAM PARTITION FRACTIONS
HTWOS provides inventories for a limited number of WTP SSW streams. The largest volume
of SSW generated from WTP operations is “other debris” waste which includes pumps, agitators,
melter components, etc. This waste stream is not specifically reported by HTWOS; therefore,
partition fractions were developed using detailed information available in Appendix C of
24590-WTP-RPT-ENS-10-010, “WTP Estimate of Secondary Radioactive Solid Waste
Generation” (10-010) and in Section 3 of 24590-WTP-RPT-ENS-10-009, “Secondary Waste
Estimates for WTP HVAC HEPA Filters” (10-009) to allocate WTP SSW inventory reported by
HTWOS to each of the following waste streams:
HEPA filters
IX resin
LAW and HLW carbon adsorber beds
HLW silver mordenite
Other debris.
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Appendix A of this data package includes a comprehensive table of these inventories as well as
the partitioning fractions used to generate them. The methodology for developing these
partitioning fractions is based on simple ratios. Using 137 Cs from a HEPA filter as an example,
the partitioning fraction was computed as follows:
Partitioning Fraction = Curies of 137Cs on HEPA
Total Curies of 137Cs in WTP SSW
A comparison of the HTWOS partitioning fractions developed from Run Case 7 to the
partitioning fractions developed from the 10-010 and 10-009 documents show very different
distributions of 129I and 99Tc in “like” WTP SSW streams (Table 6-1 and Table 6-2). HTWOS
reports most of the 129I inventory present in WTP SSW to the carbon adsorber beds (98%)
whereas the 10-010 reports only 32% to the carbon adsorber beds and the balance to HLW silver
mordenite absorbent. For 99Tc, HTWOS reports about half of the WTP SSW inventory to HEPA
filters and the other half to IX resins whereas the 10-009 reports almost all of the 99Tc to HEPA
filters (88%) with the remainder going to IX resin.
Table 6-1. 10-010 Partitioning Fractions for Waste Treatment and
Immobilization Plant Secondary Solid Waste Streams.
Waste Stream 29I 137Cs 90Sr 99Tc Cr Hg Pb
High-Efficiency Particulate Air filters 1% 51% 66% 88% 94% 0% 61%
Ion Exchange resin 0% 9% 0% 12% 5% 0% 20%
Low-Activity Waste and High-Level Waste
carbon adsorber beds 36% 0% 0% 0% 0% 100% 0%
High-Level Waste silver mordenite absorbent 62% 0% 0% 0% 0% 0% 0%
Other debris 0% 40% 34% 1% 0% 0% 19%
Table 6-2. Hanford Tank Waste Operations Simulator Partitioning Fractions for
Waste Treatment and Immobilization Plant Secondary Solid Waste Streams.
Waste Stream 29I 137Cs 90Sr 99Tc Cr Hg Pb
High-Efficiency Particulate Air filters 0% 2% 100% 45% 98% 0% 97%
Ion Exchange resin 0% 98% 0% 55% 2% 0% 3%
LAW and HLW carbon adsorber beds 98% 0% 0% 0% 0% 100% 0%
HLW silver mordenite absorbent 2% 0% 0% 0% 0% 0% 0%
Other debris N/A N/A N/A N/A N/A N/A N/A
HLW = High-Level Waste LAW = Low-Activity Waste N/A = not applicable
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The partitioning fractions used in the 10-010 and 10-009 report and by HTWOS are based on the
“Flowsheet Bases, Assumptions, and Requirements” (BARD); however, the 10-010 report
applies cleaning factors to the resulting contaminant inventories retained on all SSW stream
components. As such, the partitioning fractions developed from the 10-010 and 10-009 reports
are based on much lower inventories than those reported by HTWOS, attributing to differences
in the partitioning fractions shown in Tables 6-1 and 6-2. For analysis purposes, the
recommendation for the 2017 IDF PA would be to evaluate a range of distributions of key
contaminants in WTP SSW streams that accommodates for differences in the two partitioning
methodologies.
The partitioning fractions developed from Appendix C of the 10-010 and Section 3 of the 10-009
reports were applied to the WTP SSW inventory reported by HTWOS and a comparison of
several key contaminants for each run case was performed. This comparison shows that Run
Case 7 (presented in Table 6-3) is reasonably bounding and is therefore assumed to be the
representative case for analysis purposes. Inventory distributions based on HTWOS partition
fractions are shown in Table 6-4 for comparison purposes. No comparative inventory from the
TC&WM EIS is provided since the TC&WM EIS did not analyze WTP SSW streams at this
same level of detail. Volume estimates for each of these detailed WTP SSW streams are
presented in Section 8.2.
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Table 6-3. Run Case 7 Contaminant Inventory for Waste Treatment and Immobilization Plant Secondary Solid Waste
Streams using 10-010 Partitioning Fractions.
Waste Stream Debris/Non-Debris 129-I 137-Cs 90-Sr 99-Tc Cr Hg Pb
High-Efficiency Particulate Air Filters Debris 0.13 2,031.17 17.29 17.45 699.62 0.00 7.27
Ion Exchange Resin Non-Debris 0.02 370.76 0.02 2.36 39.77 0.02 2.33
Low-Activity Waste and High-Level Waste Carbon Beds Non-Debris 4.42 0.00 0.00 0.00 0.00 1,001.95 0.00
Other Debris Debris 0.00 1,595.89 8.98 0.11 3.47 0.00 2.31
High-Level Waste Silver Mordenite Absorbent Non-Debris 7.56 0.00 0.00 0.00 0.00 0.01 0.00
Secondary Solid Waste Total 12.12 3,997.82 26.29 19.92 742.86 1,001.98 11.91
Table 6-4. Run Case 7 Contaminant Inventory for Waste Treatment and Immobilization Plant Secondary Solid Waste
Streams using Hanford Tank Waste Operations Simulator Partitioning Fractions.
Waste Stream Debris/Non-
Debris 129-I 137-Cs 90-Sr 99-Tc Cr Hg Pb
High-Efficiency Particulate Air Filters Debris 0.00 71.41 26.29 8.99 731.67 0.00 11.61
Ion Exchange Resin Non-Debris 0.00 3,926.41 0.00 10.93 11.19 0.00 0.30
Low-Activity Waste and High-Level Waste Carbon Beds Non-Debris 11.82 0.00 0.00 0.00 0.00 1,001.98 0.00
Other Debris Debris N/A N/A N/A N/A N/A N/A N/A
High-Level Waste Silver Mordenite Absorbent Non-Debris 0.30 0.00 0.00 0.00 0.00 0.00 0.00
Secondary Solid Waste Total 12.12 3,997.82 26.29 19.92 742.86 1,001.98 11.91
NA = not applicable
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7.0 NON-WASTE TREATMENT AND IMMOBILIZATION PLANT-GENERATED
WASTE INVENTORY ESTIMATES
7.1 FAST FLUX TEST FACILITY DECOMMISSIONING WASTE INVENTORY
ESTIMATE
Table 7-1 includes the inventory estimates for FFTF decommissioning waste which are based on
the TC&WM EIS FFTF Decommissioning Alternative 2 identified in the TC&WM EIS Record
of Decision.
Table 7-1. Fast Flux Test Facility Decommissioning Inventory Estimates for Waste
Going to Integrated Disposal Facility1.
137Cs
Ci
14C
Ci
3H
Ci
99Tc
Ci
Cr
Kg
Pb
Kg
U
Kg
Sodium residuals2 1.43E-03 0.00E+00 2.29E+00 0.00E+00 5.72E-03 4.30E-03 2.86E-02
Secondary waste 1.43E-03 6.33E-04 3.58E-07 1.48E-02 1.79E-03 1.34E-03 4.09E-03
Total3 2.86E-03 6.33E-04 2.29E+00 1.48E-02 7.50E-03 5.64E-03 3.27E-02
Total4 9.61E-04 6.29E-04 1.60E-01 1.48E-02 N/A N/A N/A
1 Table D-80 from Appendix D of DOE/EIS-0391, “Final Tank Closure and Waste Management Environmental Impact
Statement for the Hanford Site, Richland, Washington.” 2 The inventory for approximately 15,142 liters (4,000 gallons) of sodium residuals which includes Fast Flux Test
Facility components (e.g., the reactor and miscellaneous traps). 3 Assumed decay date of September 2003 consistent with Tables D-75 and D-76 of DOE/EIS-0391.
4 Radionuclides decayed to January 1, 2051 (assumed Integrated Disposal Facility closure date).
N/A = not applicable
7.2 SECONDARY WASTE MANAGEMENT LOW-LEVEL WASTE AND MIXED
LOW-LEVEL WASTE INVENTORY ESTIMATE
Table 7-2 includes the inventory estimates for secondary waste based on Waste Management
Alternative 2 reported in the TC&WM EIS. Secondary waste management LLW includes
workers’ personal protective equipment, tools, tank farm activity waste, and other contaminated
waste materials such as secondary LLW and MLLW from operation of:
LLBG 218-W-5, trenches 31 and 34 (TC&WM EIS assumes that LLBG trench 31 and 34
operate through 2050, which is reasonably consistent with the PA assumption that the
IDF operates through 2051)
Waste Receiving and Processing Facility
T Plant complex.
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Table 7-2. Secondary Waste Management Low-Level Waste and Mixed Low-Level Waste Inventory Estimates for
Waste Going to Integrated Disposal Facility1.
129I 137Cs 14C 3H
233U, 234U, 235U, 238U
237Np 239Pu, 240Pu
90Sr 99Tc Cr Hg Pb
Ci Ci Ci Ci Ci Ci Ci Ci Ci Kg Kg Kg
Secondary
Waste2 1.43E-05 1.04E+00 4.04E-05 3.03E+01 1.05E-03 6.17E-06 1.86E+00 6.28E+00 9.95E-02 1.39E+01 2.29E+00 2.32E+02
Secondary
Waste3 1.43E-05 3.28E-01 4.02E-05 1.82E+00 1.05E-03 6.17E-06 1.86 1.88E+00 9.95E-02 N/A N/A N/A
1 Table D-83 from Appendix D of DOE/EIS-0391, “Final Tank Closure and Waste Management Environmental Impact Statement for the Hanford Site, Richland,
Washington.” 2 Radionuclides assumed decayed to January 1, 2001 consistent with decay date for tank waste.
3 Radionuclides decayed to January 1, 2051 (assumed Integrated Disposal Facility closure date).
N/A = not applicable
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7.3 ONSITE NON-CERCLA NON-TANK LOW-LEVEL WASTE AND MIXED
LOW-LEVEL WASTE
Table 7-3 and Table 7-4 include inventory estimates for onsite non-CERCLA non-tank LLW and
MLLW as reported in the TC&WM EIS. Onsite non-CERCLA non-tank LLW and MLLW
includes the following onsite generators:
Central Waste Complex
Plutonium Finishing Plant
T Plant complex
Waste Encapsulation and Storage Facility
WRAP
Groundwater sampling activities
Pacific Northwest National Laboratory (PNNL)
Cold Vacuum Drying Facility
Canister Storage Building, and
Liquid Waste Processing Facilities (LERF, ETF, SALDS, and Treated Effluent Disposal
Facility).
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Table 7-3. Onsite Non-CERCLA Non-Tank Low-Level Waste and Mixed Low-Level Waste Radioactive Constituents
of Potential Concern Inventory1.
129I 137Cs 14C 3H 233U, 234U, 235U, 238U 237Np 239Pu, 240Pu 90Sr 99Tc
Curies
CH- and RH-LLW 9.98E-05 1.36E+03 8.17E-01 2.68E+03 2.24E-01 4.38E-05 4.22E+00 1.75E+03 7.95E-01
CH- and RH-MLLW 1.22E-03 1.35E+03 6.88E-03 8.28E+02 5.12E-01 7.33E-03 3.81E+00 1.73E+03 4.17E-01
Total2 1.32E-03 2.71E+03 8.24E-01 3.51E+03 7.36E-01 7.37E-03 8.03E+00 3.48E+03 1.21E+00
Total3 1.32E-03 8.56E+02 8.19E-01 2.11E+02 7.36E-01 7.37E-03 8.03E+00 1.04E+03 1.21E+00
1 Table D-84 from Appendix D of DOE/EIS-0391, “Final Tank Closure and Waste Management Environmental Impact Statement for the Hanford Site, Richland,
Washington.” 2 Radionuclides assumed decayed to January 1, 2001 consistent with decay date for tank waste.
3 Radionuclides decayed to January 1, 2051 (assumed Integrated Disposal Facility closure date).
CERCLA = Comprehensive Environmental Response, Compensation, and Liability Act of 1980 MLLW = Mixed Low-Level Waste
CH = Contact Handled LLW = Low-Level Waste RH = Remote-Handled
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Table 7-4. Onsite Non-CERCLA Non-Tank Low-Level Waste and Mixed Low-Level
Waste Chemical Constituents of Potential Concern Inventory1.
Contact Handled- and Remote-Handled-Mixed Low-Level Waste (Kilograms)
Acetonitrile 3.91E+00
Arsenic (As) 6.70E+00
Benzene 1.02 E+00
Boron (B) 3.66 E+00
Butanol (N-butyl Alcohol) 1.39E-03
Cadmium (Cd) 4.95E+01
Chromium (Cr) 1.80E+02
Fluorine (F) 2.74E+02
Lead (Pb) 2.58E+04
Manganese (Mn) 4.76E+01
Mercury (Hg) 8.99E+01
Molybdenum (Mo) 9.39E-05
Nickel (Ni) 1.97 E+00
Nitrate (NO3) 2.97E+03
Polychlorinated Biphenyls 2.50E+01
Silver (Ag) 7.80E+01
Strontium (Sr) 3.13 E+00
Total Uranium (U) 9.48E-01
2,4,6-Trichlorophenol Not reported
Adapted from Table D-85 from Appendix D of DOE/EIS-0391, “Final Tank Closure and Waste Management Environmental
Impact Statement for the Hanford Site, Richland, Washington.”
Note: Inventories predicated on assumption that onsite Non-Comprehensive Environmental Response, Compensation, and
Liability Act of 1980 (CERCLA) non-tank Low-Level Waste and Mixed Low-Level Waste would be generated through 2035
and Integrated Disposal Facility would begin to receive waste in 2009 which is approximately the same operational duration
assumed for the Integrated Disposal Facility Performance Assessment.
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8.0 INTEGRATED DISPOSAL FACILITY WASTE VOLUME METHODOLOGY
As a result of treating tank waste at WTP, the IDF will receive significant volumes of MLLW
and LLW as follows:
ILAW glass
LAW melters
WTP SSW
ETF-generated SSW.
Additionally, the IDF will receive:
Secondary Waste Management LLW and MLLW
FFTF Decommissioning waste
Onsite non-CERCLA non-tank LLW and MLLW.
Disposal volume estimates for ILAW glass waste were developed using the model results from
HTWOS based on results from Run Case 7 and the sensitivity cases (Run Cases 8B, 9, 10A, and
10B). The data necessary for a mechanistic model of ILAW volumes as a function of feed rates
and glass compositions allow reasonably detailed estimates for ILAW glass volumes.
For other waste streams, a similar level of information is not available; in some cases, the
process engineering is in an early stage of design and review. For these other waste streams,
one approach for estimating waste stream volumes would be to divide the total waste stream
inventory by a waste acceptance criterion or by an assumed waste loading. For the purposes of
analysis, this data package provides reasonable estimates for as-generated waste stream volumes
using the most currently available information from Table B-1 of
24590-WTP-RPT-ENS-10-010.
As-generated volume estimates for secondary waste management LLW and MLLW and onsite
non-CERCLA non-tank LLW and MLLW were based on forecasted estimates from
HNF-EP-0918, Rev. 24, “Solid Waste Integrated Forecast Technical (SWIFT) Report FY2014 -
FY2050, 2014.0.”
8.1 IMMOBILIZED LOW-ACTIVITY WASTE GLASS WASTE VOLUME
ESTIMATES
The ILAW glass packages are stainless steel cylinders that have outside container dimensions of
approximately 2.3 meters in height and 1.22 meters in diameter (7.5 feet in height and 4.0 feet in
diameter). The density of ILAW glass is assumed to be 2.58 metric tons per cubic meter with
each package containing 5.51 metric tons of glass (TC&WM EIS, Appendix E; RPP-17152,
Rev. 9, “Hanford Tank Waste Operations Simulator (HTWOS) Version 7.7 Model Design
Document”).
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Release modeling for ILAW waste forms requires information related to the geometry, number,
and surface area of the waste containers. Table 8-1 includes volume and container estimates for
ILAW glass which are based on HTWOS results for each run case.
Table 8-1. Volume Estimates for Immobilized Low-Activity Waste Glass.
Run Case Number of ILAW Containers ILAW Glass Volumeg (m3)
7 130,584a 278,797
8B 131,610b 280,987
9 127,530c 272,277
10A 108,128d 230,853
10B 107,309e 229,105
TC&WM EIS 92,250f 213,000f
a SVF-4092, “IDF PA Case 7 - Current Information Case - Mass Balance, MMR-50049.”
b SVF-4094, “IDF PA Case 8B - Tc_Tc-99 Removal from LAW Vitrification Off-Gas Condensate - Mass Balance,
MMR-50051.” c SVF-4095, “IDF PA Case 9 - Removal of LAWPS - Mass Balance, MMR-50052.”
d SVF-4096, “IDF PA Case 10A - Single Pass Tc_Tc-99 Retention in ILAW Glass of 32% - Mass Balance, MMR-50053.”
e SVF-4097, “IDF PA Case 10B - Recycle Pass Tc_Tc-99 Retention in ILAW Glass of 68% - Mass Balance, MMR-50054.”
f DOE/EIS-0391, Table 4-85, “Final Tank Closure and Waste Management Environmental Impact Statement for the Hanford
Site, Richland, Washington” (TC&WM EIS). g Estimated based on Immobilized Low-Activity Waste container internal volume of 2.135 m3 per RPP-17152, Rev. 12,
“Hanford Tank Waste Operations Simulator (HTWOS) Version 8.1 Model Design Document.”
ILAW = Immobilized Low-Activity Waste
Overall, the run cases show an increase in the number of ILAW containers of approximately 15
to 30% when compared to the TC&WM EIS Case. These increases are due to changes that
occurred in the HTWOS model assumptions between Revision 3 of ORP-11242 that applies to
TC&WM EIS Case and Revision 7 of ORP-11242 that applies to the 2017 IDF PA run cases.
The revised assumptions for caustic leaching contribute to the increase in the number of ILAW
containers as well as two additional factors which include a revised LAW glass model and a new
liquid/solid equilibrium model. The revised LAW glass model used in HTWOS is similar to the
model used by WTP in their dynamic modeling. Also, some of the wash and leach factors were
replaced with a thermodynamic calculation for selected waste species which more accurately
forecast liquid/solid distribution as waste is mixed, concentrated, and/or treated over the course
of the WTP mission (RPP-17152, Rev. 12).
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8.2 AS-GENERATED WASTE TREATMENT AND IMMOBILIZATION PLANT
SECONDARY SOLID WASTE VOLUME ESTIMATES
The as-generated WTP SSW volume estimates associated with the operation of the WTP facility
are based on waste generation information provided in Table B-1 of
24590-WTP-RPT-ENS-10-010.
From this information, the LLW and MLLW volumes were estimated as the sum of each
individual waste stream volume computed as follows:
V(MLLW, LLW) = Waste Volume (m3) × Mission Duration (years)
Disposal Interval (years)
where the mission duration of WTP operations was assumed to be 28 years (2019 through 2047)
per Revision 6 of ORP-11242.
Table B-1 of 24590-WTP-RPT-ENS-10-010 further classifies WTP SSW as debris or non-debris
waste. Debris waste is expected to be volume-reduced and/or macroencapsulated, whereas
non-debris is expected to be particulate-sized material that would be stabilized into a
cementitious waste form prior to disposal at the IDF. Available treatment and disposal options
are conditional based on the contaminant levels in the original materials. Particulate-sized
material designed to capture mercury and halides pose a treatment and disposal challenge that
must be addressed. The 2017 IDF PA can be used as a tool to evaluate different treatment and
disposal options for these waste streams. Table 8-2 provides the waste type designation of debris
versus non-debris waste along with the as-generated volumes for each WTP SSW stream
identified in Section 6.1.1 which includes:
HEPA filters
IX resin
LAW and HLW carbon adsorber beds
HLW silver mordenite
Other debris.
As discussed in Section 6.1.1, inventory partitioning information from HTWOS and the 10-010
and 10-009 reports suggest that disproportionate amounts of key contaminants report to these
waste streams. Therefore, volume estimates associated with these waste streams over the course
of the WTP mission are needed to determine if concentration levels of these key contaminants
are important to the overall performance of the IDF system.
Waste volumes associated with the operation of LAWPS were considered and compared to those
generated by WTP operating without LAWPS. As a result, SSW volumes from the LAWPS
facility were found to be enveloped by the WTP SSW volumes; therefore, for analysis purposes,
separate volume estimates for LAWPS SSW are not being considered in the 2017 IDF PA.
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Table 8-2. Volume Estimates for Waste Treatment and Immobilization Plant Secondary
Solid Waste Streams.
Waste Treatment and
Immobilization Plant Secondary
Solid Waste Debris Stream1
Number of Containers
Generated Over
Mission Duration Container Type2,3
Total Mission
Volume4,5
(m3)
HEPA filters (1-year) 2,045 Drums 524
HEPA filters (5-year) 5,085 Drums 1,308
Other debris 60,309 Drums/assorted boxes 26,546
Debris total 67,439 N/A 28,378
Waste Treatment and
Immobilization Plant Secondary
Solid Waste Non-Debris Stream
Number of Containers
Generated Over
Mission Duration Container Type2,3
Total Mission
Volume4 (m3)
Ion Exchange resin 112 High Integrity Containers 686
LAW and HLW carbon beds 4,424 Drums 1,137
HLW silver mordenite absorbent 403 Drums 104
Non-Debris total 4,939 N/A 1,927
1 Excludes waste volumes for:
LAW melters and ETF-generated secondary solid waste since those volumes are estimated separately
HLW melters which are assumed to be placed in interim onsite storage until final dispositions decisions are made and
implemented. 2 Drums are 0.257 m3.
3 High Integrity Containers are 6.125 m3 (6 ft × 6 ft × 6 ft).
4 Volumes based on outside container dimension reported in Appendix B of 24590-WTP-RPT-ENS-10-010, “WTP Estimate
of Secondary Radioactive Solid Waste Generation.” 5 Waste Treatment and Immobilization Plant mission duration = 28 years.
ETF = Effluent Treatment Facility HLW = High-Level Waste N/A = not applicable
HEPA = High-Efficiency Particulate Air LAW = Low-Activity Waste
A number of standard pre-approved waste disposal packages are in use at the Hanford Site.
When practical, waste is packaged in these standard pre-approved packages. Some waste
streams (for example, spent melters) present unique circumstances that dictate nonstandard
packaging. The following types of waste packages are expected to be used by the WTP project
for transporting and/or disposing of WTP SSW (24590-WTP-PL-PENG-14-0006, “Secondary
Wastes Compliance Plan”):
Lab packs
16-gallon drums
30-gallon drums
55-gallon drums
85-gallon drums
2 ft × 2 ft × 6 ft Type A box
4 ft × 4 ft × 8 ft Type A box
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5 ft × 5 ft × 9 ft Type A box
8 ft × 8 ft × 20 ft IP1 conex or sea-land type box
LAW locally shielded melter (see Section 9.3)
High Integrity Containers (6 ft × 6 ft × 6 ft)
Other containers.
8.3 BACKGROUND-INDUSTRY STANDARDS FOR WASTE TREATMENT
The current plan for disposing of waste at IDF involves the use of an offsite treatment facility
experienced in treating Hanford waste streams for onsite disposal. Standard practices for treating
waste include stabilization, macroencapsulation as well as some degree of volume reduction via
repackaging and compaction depending on the type and category of waste received. The general
strategy for treating both LLW and MLLW provides a basis for developing WTP SSW treatment
and disposal consideration and assumptions.
8.3.1 Low-Level Waste
Category 1 and Category 3 LLW debris volumes are reduced in order to decrease the volume of
waste shipped for disposal and ensure optimal waste form for disposal. Volume reduction is
accomplished by both thermal (Category 1 LLW) and non-thermal processes (Category 3 LLW).
The thermal process utilizes Bulk Process Units that are large, refractory lined ovens. The Bulk
Process Units operate at 1,800 degrees Fahrenheit. This temperature is sufficient to ignite and
burn all combustible material and results in typical volume reductions of 30:1 to 100:1. This
type of treatment is generally reserved for combustible Category 1 LLW and would not be
performed if residual ash and debris was expected to exceed Category 3 limits.
The non-thermal processes include size reduction, compaction, and decontamination for free
release. The treatment facility uses a super-compactor to compact the waste drums which are
then overpacked into either an overpack drum or box prior to disposal. The typical volume
reductions range from 2:1 to 10:1 depending on debris type. Cylindrical components with metal
frames (e.g., HEPA filters) or thin, hollow shells would tend to be compacted more than
components with less internal void volume.
8.3.2 Mixed Low-Level Waste
Category 1 and Category 3 MLLW are treated via non-thermal processes including
macroencapsulation (debris) and stabilization (non-debris). The facility’s macroencapsulation
process is specifically designed to treat hazardous debris and radioactive lead solids in
compliance with Title 40, Code of Federal Regulations, Part 268.45, “Treatment Standards for
Hazardous Debris” (40 CFR 268.45) and Title 40, Code of Federal Regulations, Part 268.40,
“Applicability of Treatment” (40 CFR 268.40) in preparation for disposal at a mixed waste
Subtitle C landfill.
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The macroencapsulation process involves sorting, segregating, and super-compacting mixed
low-level debris wastes, thus resulting in a volume reduction ratio of approximately 2.5:1. Like
LLW, volume reduction of MLLW debris is dependent on the structure of the debris. The
facility estimates that it can often achieve volume reduction ratios of 2.5:1 by shearing and
repackaging components prior to macroencapsulation. Stabilization is used for mixed low-level
non-debris wastes and is accomplished by introducing reagents into the waste stream producing a
homogeneous, stabilized, final product.
Stabilization has been defined as the Best Demonstrated Available Technology for treating a
wide range of RCRA listed, characteristic waste streams. Analysis of resulting waste forms will
meet the concentration-based (performance) standards or the stabilization treatment technology
requirements to meet RCRA LDR.
8.4 WASTE TREATMENT AND IMMOBILIZATION PLANT SECONDARY SOLID
WASTE TREATMENT AND DISPOSAL CONSIDERATIONS AND
ASSUMPTIONS
The strategy assumed for treating and disposing of secondary waste streams generated from
WTP operations is generally based on industry standards for treating LLW and MLLW (debris
and non-debris) as discussed in Sections 8.3.1 and 8.3.2.
Debris streams will undergo some type of volume reduction via compaction/supercompaction,
sorting, and repackaging at an offsite treatment facility prior to disposal at the IDF. As a result,
these waste streams may become somewhat more concentrated at the time of disposal; however,
the treatment facility will not generate waste streams that exceed the waste acceptance criteria
limits at the IDF (i.e., greater-than-Category 3).
For non-debris waste streams, the disposal volumes will increase slightly based on repackaging
and treatment methods that include the addition of dry materials for stabilization purposes.
Treatment and packaging of all WTP SSW will occur at an offsite commercial vendor facility
and the resulting waste packages will be transported to the IDF for disposal. For analysis
purposes, additional assumptions associated with the treatment, packaging, and disposal volumes
for individual waste streams are described below.
For IX resins, LAW and HLW carbon adsorber beds, and HLW silver mordenite absorbent these
assumptions are:
IX resins would be non-debris MLLW which would be dewatered at WTP before being
transported in High Integrity Containers offsite for treatment. At the treatment facility,
the resin would be repackaged into carbon steel 55-gallon drums with a stabilization
grout for RCRA metals and Category 3 radioactive waste containment using a
Hanford-approved grout formulation meeting regulatory criteria.
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Carbon adsorber beds and HLW silver mordenite absorbent would also be non-debris
MLLW, which from a treatment perspective, contain potentially problematic amounts of
Hg and 129I. The conservative recommendation for disposition of this waste is to dispose
of it at IDF. The beds would be transported to a local offsite treatment facility where
they would be repackaged into carbon steel 55-gallon drums with a stabilization grout for
RCRA metals and Category 3 radioactive waste containment using a Hanford-approved
grout formulation that meets regulatory criteria.
Based on literature reviews and consultation with waste treatment experts, the
stabilization of non-debris waste streams would result in volume increases ranging from
1.5 to 3.0 times the as-generated waste volumes (“Performance Testing of Grout-Based
Waste Forms for the Solidification of Anion Exchange Resins” [ORNL 1990];
WHC-EP-0375, “Engineering Study for the Treatment of Spent Ion Exchange Resin
Resulting from Nuclear Process Applications; PNNL-19681, “Tc-99 Ion Exchange Resin
Testing”). Using a multiplier on the lower end of this range would result in an increased
concentration of contaminants within each disposal package and would be a conservative
estimate of the source term in the 2017 IDF PA. For analysis purposes, a 1.5 multiplier
should be applied to all non-debris waste stream volumes. This assumption is reasonably
consistent with the cementitious waste-to-grout volume ratios discussed in Section 8.4 for
ETF-generated SSW (0.693 L waste/ L grout).
For HEPA filters, these assumptions are:
HEPA filters would be MLLW debris. All HEPA filters will be received at an offsite
treatment facility in carbon steel 55-gallon drums where they will be compacted into
“pucks” at an approximate compaction ratio of 10:1.
Up to 25 pucks could be placed into 4 ft × 4 ft × 6 ft disposal boxes and
macroencapsulated with grout to meet LDR requirements for RCRA constituents8. This
macroencapsulation process would meet Category 3 stabilization requirements, which
exceed Category 1 requirements.
The projected volume of debris waste, excluding HEPA filters, is approximately
28,000 m3. The WTP secondary waste forecast suggests that more than a third of the
debris is compactible debris. Approximately 25% of the projected waste is compactible,
Category 1 LLW that is expected to have a higher compaction ratio than Category 3
MLLW, but also have lower concentrations prior to compaction.
For other debris wastes (excludes HEPA filters), these assumptions are:
Assuming a compaction ratio of 10:1 for the compactible, Category 1 LLW debris and a
compaction ratio of 2.5:1 for all other debris waste, it is recommended that an average
8 The work authorization process implemented at the treatment facility determines the allowable number of pucks
based on waste stream characterization information provided by the waste generator at the time of shipment to the
treatment facility. Disposal box limits (after drums are compacted into pucks at a compaction ratio of
approximately 10:1) are closely managed such that Category 3 limits are not exceeded.
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compaction ratio for the remaining non-HEPA filter debris waste be 5:1
(0.25×10+0.75×2.55).
Note that these reduction factors for debris waste are based on 5 years of actual WRPS SSW
treatment data provided by experts in the waste treatment industry (e-mail from R. Grondin to
R. L. Keller “waste streams slated for offsite” [Grondin, R., 2016-02-18]).
8.5 LOW-ACTIVITY WASTE MELTER VOLUME ESTIMATES
The LAW melters from WTP operations would be disposed of at IDF as MLLW. As such, LAW
melters would require treatment to meet LDR requirements under RCRA.
Up to 18 LAW melters would be required to be void filled with grout, macroencapsulated, or
packaged within in an overpack prior to disposal (RPP-RPT-58204).
According to Tank Closure Alternative 2B from the TC&WM EIS, an estimate of 31 LAW
melters would be disposed of at the IDF. This represents the maximum quantity of LAW melters
that would result from WTP operations and is driven by the expanded ILAW glass operations
and vitrification treatment processes. Additionally, the TC&WM EIS reports 7.620 m3 of
residual glass waste could remain in each melter at the time of disposal. This volume is based on
the glass tank surface dimension of the LAW melter and the maximum glass pool operating
depth (24590-LAW-MOD-LMP-00002, “Data Sheet Low Active Waste Melter 2”).
Two possible disposal volume estimates for LAW melters are presented in Table 8-3 based on
the melter’s physical dimensions and the melter’s overpack dimensions (as assumed in the
TC&WM EIS).
Table 8-3. Volume Estimates for Low-Activity Waste Melters and Residual Glass
Volume.
Waste Type
Number of Melters
Generated over the
WTP Mission
Length
(m)
Width
(m)
Height
(m)
Melter
Volume
(m3)
Mission
Melter
Volume
(m3)
Residual Glass
Waste Volume
over the WTP
Mission (m3)
LAW Melters1 18 6.65 9.32 4.83 299 5,382 137
LAW Melters
Overpack2 31 6.79 9.38 4.86 310 9,610 236
1 RPP-RPT-58204, “Spent/Failed Low-Activity Waste Melter Transport System Evaluation Report,” Table 2-1.
2 DOE/EIS-0391, “Final Tank Closure and Waste Management Environmental Impact Statement for the Hanford Site,
Richland, Washington,” Appendix E.
LAW = Low-Activity Waste WTP = Waste Treatment and Immobilization Plant
Consistent with the TC&WM EIS analysis, HLW melters are assumed to be placed in interim
onsite storage until final dispositions decisions are made and implemented.
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8.6 EFFLUENT TREATMENT FACILITY-GENERATED SECONDARY SOLID
WASTE
Secondary liquid wastes resulting from WTP operations, 242-A evaporator campaigns, and
CH-TRU tank retrievals will be treated at the ETF. Liquid waste received by the ETF is
processed via two treatment trains. The main treatment train is designed to remove radioactive
and hazardous constituents using filtration, ultraviolet oxidation, degasification, reverse osmosis,
and ion-exchange systems. Clean water meeting discharge permit requirements is discharged to
the SALDS location north of 200 West Area. The secondary treatment train processes
wastewater rejected from the main treatment train. The secondary train concentrates the waste to
a brine and then dries the waste using a thin-film drying process. The current plan for the liquid
MLLW resulting from WTP operations, 242-A evaporator, and CH-TRU retrieval is to stabilize
the concentrate (brine) that results from the secondary treatment train at the ETF and send the
resulting cementitious waste form to the IDF for disposal.
Plans for solidifying secondary liquid waste from WTP, condensate from the 242-A evaporator,
and liquid waste resulting from retrieval of CH-TRU tanks at the ETF in preparation for disposal
at the IDF are currently being evaluated. The information needed to estimate this waste volume
based on these plans is still being developed and will not be available until a later time.
Therefore, ETF-generated SSW volumes going to the IDF were based on the liquid volumes
provided by HTWOS (Table 8-4) and the following simplifying assumptions:
The waste form will be a cementitious waste form (i.e., Cast Stone grout) with a monolith
density of 1.8 kg/L and a water-to-dry mix ratio of 0.6 (Tables 2-1 and D-4 of
PNNL-22747/SRNL-STI-2013-00465, “Supplemental Immobilization of Hanford
Low-Activity Waste: Cast Stone Screening Tests”). The water-to-dry mix ratio of 0.6
was selected because of improved flow characteristics and increased waste loading.
The liquid feed streams from WTP will be converted to a brine at ETF prior to being
blended with the dry mix materials. The volume ratios of brine to feed are based on
Table 1 of HNF-58821, “Effluent Treatment Facility Mass Balance Calculation for
DFLAW Mission”). The brine-to-feed volume ratio for the Direct Feed Low Activity
Waste (DFLAW) Effluent Management Facility (EMF)/CS source in Table 1 is
applicable to the WTP and TRU process streams. The brine-to-feed volume ratio for the
242-A evaporator process condensate is reported separately. As shown, the brine-to-feed
volume ratios determined from Table 1 are:
o 242-A process condensate = 0.00232 (gallons brine/gallons feed)
o DFLAW EMF/CS = 0.00926 (gallons brine/gallons feed).
For DFLAW EMF/CS, there are 838 grams of water per liter of waste (page 540 of
HNF-58821).
Using the water-to-dry mix ratio (0.6), the monolith density (1.8 kg/L), the water
concentration from the DFLAW EMF/CS (838 g/L), and the density of the DFLAW
EMF/CS stream (1.2 kg/L), the ratio of waste to grout was approximated as
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0.693 L waste/ L grout. This ratio was then used to estimate the ETF-generated SSW
volume going to the IDF for each HTWOS run case.
Table 8-4 shows the liquid waste volumes generated during the entire WTP mission that will be
sent to LERF and processed at ETF. The resulting estimated solid waste volumes would be
disposed at the IDF. Several HTWOS run cases are provided to illustrate the potential range of
grouted waste volumes to be disposed at the IDF. Although these estimates are based on the
most current information, they will be updated as new information becomes available.
Table 8-4. Effluent Treatment Facility-Generated Secondary Solid Waste Disposal
Volume Estimates.
Run Case
WTP-
TO-
LERF
(gallons)
242-A-TO-LERF
(gallons)
TRU-
PROCESSING-
TO-LERF
(gallons)
Total
Volume
to LERF
(gallons)
Cementitious
Waste Volume
going to the
IDF (m3)*
Case 7: Current
Information Case 3.52E+08 7.07E+07 4.42E+06 4.27E+08 1.89E+04
Case 8B: Tc-99 Removal
from LAW Vitrification
Off-Gas Condensate 3.36E+08 8.00E+07 4.42E+06 4.21E+08 1.82E+04
Case 9: Removal of
LAWPS 3.15E+08 9.23E+07 4.42E+06 4.12E+08 1.73E+04
Case 10A: Single Pass
Tc-99 Retention in ILAW
Glass of 32% 3.36E+08 6.91E+07 4.42E+06 4.09E+08 1.81E+04
Case 10B: Recycle Tc-99
Retention in ILAW Glass
of 68% 3.30E+08 6.15E+07 4.42E+06 3.96E+08 1.77E+04
* Volumes approximated following steps 1-3:
1. Converting each waste stream volume to its associated brine volume (= waste volume × brine-to-feed ratio)
2. Converting brine volume from gallons to liters, then dividing by the approximated waste-to-grout ratio
(0.693 L waste/ L grout)
3. Converting grouted waste volume from liters to m3.
IDF = Integrated Disposal Facility LERF = Liquid Effluent Retention Facility
ILAW = Immobilized Low-Activity Waste TRU = transuranic
LAW = Low-Activity Waste WTP = Waste Treatment and Immobilization Plant
LAWPS = Low-Activity Waste Pretreatment System
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8.7 SECONDARY WASTE MANAGEMENT LOW-LEVEL WASTE AND MIXED
LOW-LEVEL WASTE VOLUME ESTIMATES
Table 8-5 includes volume estimates for secondary waste solids from the operation of the
following facilities:
Tank farms (workers’ personal protective equipment, tools, and other contaminated
materials)
LLBG 218-W-5, trenches 31 and 34
WRAP
T Plant complex.
Table 8-5. As-Generated Secondary Waste Management Waste Volume Estimates.
Waste Type Total Volume (m3) Volume Fraction
Low-Level Waste 1,742 18%
Mixed Low-Level Waste 7,747 82%
Total 9,489 100%
Per HNF-EP-0918, Rev. 24, “Solid Waste Integrated Forecast Technical (SWIFT) Report FY2014 - FY2050,
2014.0.”
Operations activities assumed to be 2019 through 2050, which is the duration for which the Integrated Disposal
Facility is planning to receive waste.
8.8 FAST FLUX TEST FACILITY DECOMMISSIONING WASTE DISPOSAL
VOLUME ESTIMATE
The volume estimate reported in Table 8-6 for FFTF decommissioning waste is based on the
disposal volume used in the TC&WM EIS as reported in release to vadose zone input file for
FFTF Alternative 2.
Table 8-6. Fast Flux Test Facility Decommissioning Disposal Waste Volume Estimate.
Waste Stream Total Disposal Volume (m3)
Fast Flux Test Facility Decommissioning Alternative 2 1,030
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8.9 AS-GENERATED ONSITE NON-CERCLA NON-TANK LOW-LEVEL WASTE
AND MIXED LOW-LEVEL WASTE VOLUME ESTIMATES
Table 8-7 includes volume estimates for solid secondary waste from the following sources:
Central Waste Complex
Plutonium Finishing Plant
Waste Encapsulation and Storage Facility
Groundwater sampling activities
Pacific Northwest National Laboratory
Cold Vacuum Drying Facility
Canister Storage Building, and
Liquid Waste Processing Facilities (LERF, ETF, SALDS, and Treated Effluent Disposal
Facility).
Table 8-7. Onsite Non-CERCLA Non-Tank Low-Level Waste and
Mixed Low-Level Waste As-Generated Volume Estimates.
Waste Type Volume (m3)
Low-Level Waste 442
Mixed Low-Level Waste 181
Total 623
Per HNF-EP-0918, Rev. 24, “Solid Waste Integrated Forecast Technical (SWIFT) Report FY2014 - FY2050, 2014.0.”
Operations activities assumed to be 2019 through 2050, which is the duration for which the Integrated Disposal
Facility is planning to receive waste.
CERCLA = Comprehensive Environmental Response, Compensation, and Liability Act of 1980
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9.0 SUMMARY OF RESULTS
Tables 9-1 and 9-2 provide a summary of the inventory estimates derived from HTWOS. These
summary tables report inventories for a select set of radionuclide and chemical constituents that
includes 129I, 137Cs, 14C, 233U, 234U, 235U, 238U, 237Np, 239Pu, 240Pu, 3H, 90Sr, 99Tc, Cr, Hg, NO3-,
Pb, and U. Comprehensive inventory tables for all BBI constituents with radionuclides decayed
to 2008 and 2051 are included in Appendix A.
Tables 9-3 and 9-4 provide a summary of the inventory estimates from Appendix D of the
TC&WM EIS for Tank Closure Alternative 2A (Alternative 2B with 99Tc removal) to facilitate
comparisons to Tables 9-1 and 9-2. These summary tables report inventories for a select set of
radionuclide and chemical constituents that includes 129I, 137Cs, 14C, 233U, 234U, 235U, 238U, 237Np, 239Pu, 240Pu, 3H, 90Sr, 99Tc, Cr, Hg, NO3
-, Pb, and U.
Since groundwater impacts associated with disposal of MLLW and LLW at the IDF are highly
dependent on the distributions of mobile radionuclides such as 99Tc and 129I present in glass and
grout waste forms, this summary focuses primarily on the inventory and waste form distributions
of these two constituents.
9.1 INTEGRATED DISPOSAL FACILITY WASTE FORMS BASED ON HANFORD
TANK WASTE OPERATIONS SIMULATOR RUN CASES
Five HTWOS model run cases were developed to explore ranges of inventory estimates for
waste streams going to the IDF that result from processing tank waste through the WTP Facility
using different process flowsheet assumptions. Since the capture of 99Tc and 129I in the ILAW
glass is an important consideration when evaluating the performance of the IDF system, each
case was designed to evaluate a range of distributions of these contaminants in glass and grout
waste forms.
Cases 10A and 10B represent sensitivity cases that were contrived to place lower fractions of 99Tc and 129I in ILAW glass, and higher fractions into the LAW liquid off-gas stream which
would be disposed of at the IDF as ETF-generated SSW. As such, the upper limits of loading 99Tc and 129I in a cementitious waste form can be tested against waste form performance
characteristics. Since the inventory allocation is based on a single-pass WTP flowsheet
configuration and the current WTP flowsheet includes recycle, these are unlikely cases from an
operational perspective.
These cases serve as a starting point for gaining an understanding of the IDF disposal system
considering all the uncertainties associated with each IDF waste form. These uncertainties
include tank waste composition and inventory uncertainties, WTP process and operational
uncertainties, and HTWOS model/partitioning uncertainties. Other run cases are expected to
evolve based on the knowledge gained from model runs of these initial cases and maturity of the
WTP process flowsheet. Development of the WTP process flowsheet is in flux pending
technical decisions regulatory discussions.
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The key features of each HTWOS run case are described in the context of the TC&WM EIS
Case (represented by Tank Closure Alternative 2A).
Case 7 – Similar to the TC&WM EIS case except that initially the WTP Pretreatment
Facility recycle configuration is routed from LAW Vitrification back to tank farms, and
the BBI was updated (2014 vs. 2002). A fixed retention of 129I in ILAW glass of 20% is
not included; rather, it is consistent with the TC&WM EIS for the 129I retention factor of
20% for each pass, but exceeds the TC&WM EIS retention factor as a result of recycle.
This case has similar retention of 99Tc in ILAW glass as the TC&WM EIS (~98%). This
run case is the starting point for subsequent HTWOS run cases (Run Cases 8B, 9, 10A,
and 10B).
Case 8B – From an TC&WM EIS perspective, this case is the same as Case 7, except that
a 99Tc removal unit operation has been added after the SBS-WESP process to remove 99Tc at an efficiency of 99% from the LAW liquid off-gas stream prior to being recycled
to backend evaporator in the Pretreatment Facility. This removed 99Tc inventory would
not be disposed of at the IDF and represents the lower range of 99Tc inventory in both
glass and grout waste forms that would be disposed of at the IDF.
Case 9 – Similar to the TC&WM EIS case, the WTP Pretreatment Facility recycle
configuration is routed from LAW Vitrification back to the Pretreatment Facility.
Case 10A – Similar to TC&WM EIS case, 129I retention in ILAW glass is 20%; however,
the recycle efficiency is much lower than the TC&WM EIS such that 32% of 99Tc is
retained in ILAW glass (modeled in HTWOS using a single pass). Case 10A is a
contrived case. Partitioning of the constituents between other phases uses the inherent
split fractions applied in the HTWOS model without consideration of whether the product
stream could be treated using the recommended treatment method or could ultimately be
disposed in the IDF. This case exercises the process modeling tool that is available to
generate an inventory case that could be used to test the limits of the facility to meet
established performance criteria.
Case 10B – Similar to TC&WM EIS case, 129I retention in ILAW glass is 20%; however,
the recycle efficiency is somewhat lower than the TC&WM EIS such that 68% of 99Tc is
retained in ILAW glass (modeled in HTWOS using a single pass). Case 10B is a
contrived case. Partitioning of the constituents between other phases uses the inherent
split fractions applied in the HTWOS model without consideration of whether the product
stream could be treated using the recommended treatment method or could ultimately be
disposed in the IDF. This case exercises the process modeling tool that is available to
generate an inventory case that could be used to test the limits of the facility to meet
established performance criteria.
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Table 9-1. Summary of Radionuclide Constituents Inventories and Waste Form Distributions Resulting from Hanford Tank Waste Operations Simulator Run Cases (November 2014 Best-Basis Inventory with
radionuclides decayed to January 2008).
1 SVF-4092, “IDF PA Case 7 - Current Information Case - Mass Balance, MMR-50049.”
2 SVF-4094, “IDF PA Case 8B - Tc_Tc-99 Removal from LAW Vitrification Off-Gas Condensate - Mass Balance, MMR-50051.”
3 SVF-4095, “IDF PA Case 9 - Removal of LAWPS - Mass Balance, MMR-50052.”
4 SVF-4096, “IDF PA Case 10A - Single Pass Tc_Tc-99 Retention in ILAW Glass of 32% - Mass Balance, MMR-50053.”
5 SVF-4097, “IDF PA Case 10B - Recycle Pass Tc_Tc-99 Retention in ILAW Glass of 68% - Mass Balance, MMR-50054.”
6 As a result of removing Tc-99 from the LAW off-gas stream, 16,500 Ci of Tc-99 accumulate over the course of the Waste Treatment and Immobilization Plant mission. These Ci would likely be processed in High-Level Waste and would not end up at the IDF.
BBI = Best-Basis Inventory ETF = Effluent Treatment Facility HTWOS = Hanford Tank Waste Operations Simulator IDF = Integrated Disposal Facility ILAW = Immobilized Low-Activity Waste LAW = Low-Activity Waste NA = not applicable
HTWOS Run Case Constituent 129-I 137-Cs 14-C 233-U 234-U 235-U 237-Np 238-U 239-Pu 240-Pu 3-H 90-Sr 99-Tc
HTWOS BBI Inventory 2.94E+01 3.90E+07 5.51E+02 6.82E+02 2.37E+02 9.71E+00 1.15E+02 2.15E+02 4.94E+04 1.08E+04 2.82E+03 4.76E+07 2.65E+04
Units Ci %BBI %IDF Ci %BBI %IDF Ci %BBI %IDF Ci %BBI %IDF Ci %BBI %IDF Ci %BBI %IDF Ci %BBI %IDF Ci %BBI %IDF Ci %BBI %IDF Ci %BBI %IDF Ci %BBI %IDF Ci %BBI %IDF Ci %BBI %IDF
Case 71 ILAW Glass 1.65E+01 56.21% 57.51% 1.05E+04 0.03% 72.41% 0.00E+00 0.00% 0.00% 9.94E+00 1.46% 99.87% 3.01E+00 1.27% 99.76% 1.22E-01 1.25% 99.76% 1.73E+01 15.03% 99.88% 2.70E+00 1.26% 99.76% 4.48E+03 9.06% 99.87% 9.45E+02 8.75% 99.87% 0.00E+00 0.00% 0.00% 2.57E+05 0.54% 99.83% 2.64E+04 99.58% 99.78%
LAW Melters 2.38E-02 0.08% 0.08% 1.36E+01 0.00% 0.09% 0.00E+00 0.00% 0.00% 1.29E-02 0.00% 0.13% 4.25E-03 0.00% 0.14% 1.73E-04 0.00% 0.14% 2.09E-02 0.02% 0.12% 3.85E-03 0.00% 0.14% 5.94E+00 0.01% 0.13% 1.25E+00 0.01% 0.13% 0.00E+00 0.00% 0.00% 3.21E+02 0.00% 0.12% 3.75E+01 0.14% 0.14%
ETF-Generated Secondary Solid Waste 6.42E-02 0.22% 0.22% 6.70E-01 0.00% 0.00% 3.52E+00 0.64% 100.00% 1.78E-05 0.00% 0.00% 2.89E-03 0.00% 0.10% 1.21E-04 0.00% 0.10% 7.08E-05 0.00% 0.00% 2.78E-03 0.00% 0.10% 6.17E-03 0.00% 0.00% 1.28E-03 0.00% 0.00% 2.34E+00 0.08% 100.00% 9.85E+01 0.00% 0.04% 2.29E-01 0.00% 0.00%
Secondary Solid Waste 1.21E+01 41.23% 42.18% 4.00E+03 0.01% 27.49% 0.00E+00 0.00% 0.00% 1.65E-06 0.00% 0.00% 5.16E-07 0.00% 0.00% 2.10E-08 0.00% 0.00% 2.02E-06 0.00% 0.00% 4.65E-07 0.00% 0.00% 2.02E-02 0.00% 0.00% 1.98E-02 0.00% 0.00% 0.00E+00 0.00% 0.00% 2.63E+01 0.00% 0.01% 1.99E+01 0.08% 0.08%
IDF Total 2.87E+01 97.74% 100.00% 1.45E+04 0.04% 100.00% 3.52E+00 0.64% 100.00% 9.95E+00 1.46% 100.00% 3.02E+00 1.27% 100.00% 1.22E-01 1.26% 100.00% 1.73E+01 15.05% 100.00% 2.71E+00 1.26% 100.00% 4.48E+03 9.07% 100.00% 9.46E+02 8.76% 100.00% 2.34E+00 0.08% 100.00% 2.58E+05 0.54% 100.00% 2.64E+04 99.80% 100.00%
Case 8B2 ILAW Glass 1.65E+01 56.25% 57.54% 1.40E+04 0.04% 78.07% 0.00E+00 0.00% 0.00% 1.02E+01 1.50% 99.91% 2.98E+00 1.26% 99.79% 1.21E-01 1.24% 99.79% 1.72E+01 14.95% 99.89% 2.66E+00 1.24% 99.79% 4.51E+03 9.14% 99.88% 9.64E+02 8.92% 99.87% 0.00E+00 0.00% 0.00% 1.83E+05 0.39% 99.85% 9.97E+03 37.62% 99.75%
LAW Melters 1.64E-02 0.06% 0.06% 1.19E+01 0.00% 0.07% 0.00E+00 0.00% 0.00% 9.25E-03 0.00% 0.09% 3.28E-03 0.00% 0.11% 1.33E-04 0.00% 0.11% 1.92E-02 0.02% 0.11% 2.94E-03 0.00% 0.11% 5.58E+00 0.01% 0.12% 1.19E+00 0.01% 0.12% 0.00E+00 0.00% 0.00% 1.63E+02 0.00% 0.09% 1.11E+01 0.04% 0.11%
ETF-Generated Secondary Solid Waste 6.56E-02 0.22% 0.23% 6.06E-01 0.00% 0.00% 3.67E+00 0.67% 100.00% 1.79E-05 0.00% 0.00% 2.88E-03 0.00% 0.10% 1.21E-04 0.00% 0.10% 7.17E-05 0.00% 0.00% 2.77E-03 0.00% 0.10% 6.37E-03 0.00% 0.00% 1.32E-03 0.00% 0.00% 3.26E+00 0.12% 100.00% 9.37E+01 0.00% 0.05% 2.89E-02 0.00% 0.00%
Secondary Solid Waste 1.21E+01 41.24% 42.18% 3.92E+03 0.01% 21.86% 0.00E+00 0.00% 0.00% 1.68E-06 0.00% 0.00% 5.13E-07 0.00% 0.00% 2.08E-08 0.00% 0.00% 2.00E-06 0.00% 0.00% 4.61E-07 0.00% 0.00% 1.88E-02 0.00% 0.00% 1.84E-02 0.00% 0.00% 0.00E+00 0.00% 0.00% 2.63E+01 0.00% 0.01% 1.35E+01 0.05% 0.14%
Accumulator6 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 1.65E+04 62.09% NA
IDF Total 2.87E+01 97.76% 100.00% 1.79E+04 0.05% 100.00% 3.67E+00 0.67% 100.00% 1.02E+01 1.50% 100.00% 2.98E+00 1.26% 100.00% 1.21E-01 1.24% 100.00% 1.72E+01 14.97% 100.00% 2.67E+00 1.24% 100.00% 4.52E+03 9.15% 100.00% 9.65E+02 8.93% 100.00% 3.26E+00 0.12% 100.00% 1.84E+05 0.39% 100.00% 9.99E+03 37.60% 100.00%
Case 93 ILAW Glass 1.65E+01 56.26% 57.54% 9.30E+03 0.02% 75.75% 0.00E+00 0.00% 0.00% 1.17E+01 1.71% 99.87% 2.99E+00 1.26% 99.77% 1.19E-01 1.23% 99.77% 1.72E+01 14.98% 99.86% 2.65E+00 1.23% 99.76% 5.07E+03 10.25% 99.88% 1.06E+03 9.80% 99.88% 0.00E+00 0.00% 0.00% 1.38E+05 0.29% 99.77% 2.64E+04 99.63% 99.83%
LAW Melters 1.76E-02 0.06% 0.06% 1.11E+01 0.00% 0.09% 0.00E+00 0.00% 0.00% 1.48E-02 0.00% 0.13% 3.95E-03 0.00% 0.13% 1.58E-04 0.00% 0.13% 2.33E-02 0.02% 0.14% 3.50E-03 0.00% 0.13% 6.25E+00 0.01% 0.12% 1.31E+00 0.01% 0.12% 0.00E+00 0.00% 0.00% 1.72E+02 0.00% 0.12% 2.82E+01 0.11% 0.11%
ETF-Generated Secondary Solid Waste 6.03E-02 0.20% 0.21% 6.01E-01 0.00% 0.00% 2.25E+00 0.41% 100.00% 1.71E-05 0.00% 0.00% 2.89E-03 0.00% 0.10% 1.21E-04 0.00% 0.10% 7.10E-05 0.00% 0.00% 2.77E-03 0.00% 0.10% 5.73E-03 0.00% 0.00% 1.17E-03 0.00% 0.00% 3.84E+00 0.14% 100.00% 1.24E+02 0.00% 0.09% 2.16E-01 0.00% 0.00%
Secondary Solid Waste 1.21E+01 41.24% 42.19% 2.96E+03 0.01% 24.15% 0.00E+00 0.00% 0.00% 1.85E-06 0.00% 0.00% 5.14E-07 0.00% 0.00% 2.07E-08 0.00% 0.00% 2.01E-06 0.00% 0.00% 4.59E-07 0.00% 0.00% 1.40E-02 0.00% 0.00% 1.35E-02 0.00% 0.00% 0.00E+00 0.00% 0.00% 2.64E+01 0.00% 0.02% 1.64E+01 0.06% 0.06%
IDF Total 2.87E+01 97.77% 100.00% 1.23E+04 0.03% 100.00% 2.25E+00 0.41% 100.00% 1.17E+01 1.71% 100.00% 3.00E+00 1.26% 100.00% 1.20E-01 1.23% 100.00% 1.72E+01 15.00% 100.00% 2.65E+00 1.23% 100.00% 5.07E+03 10.27% 100.00% 1.06E+03 9.82% 100.00% 3.84E+00 0.14% 100.00% 1.38E+05 0.29% 100.00% 2.64E+04 99.80% 100.00%
Case 10A4 ILAW Glass 5.71E+00 19.43% 19.80% 7.89E+03 0.02% 55.55% 0.00E+00 0.00% 0.00% 9.08E+00 1.33% 98.96% 3.07E+00 1.29% 98.87% 1.25E-01 1.29% 98.87% 1.72E+01 14.91% 98.96% 2.77E+00 1.29% 98.87% 4.37E+03 8.85% 98.96% 9.34E+02 8.65% 98.96% 0.00E+00 0.00% 0.00% 2.15E+05 0.45% 98.95% 8.46E+03 31.91% 31.95%
LAW Melters 7.68E-03 0.03% 0.03% 1.04E+01 0.00% 0.07% 0.00E+00 0.00% 0.00% 1.25E-02 0.00% 0.14% 4.26E-03 0.00% 0.14% 1.73E-04 0.00% 0.14% 2.43E-02 0.02% 0.14% 3.84E-03 0.00% 0.14% 6.09E+00 0.01% 0.14% 1.29E+00 0.01% 0.14% 0.00E+00 0.00% 0.00% 2.29E+02 0.00% 0.11% 1.13E+01 0.04% 0.04%
ETF-Generated Secondary Solid Waste 1.88E+01 63.80% 65.00% 2.53E+03 0.01% 17.81% 2.53E+00 0.46% 100.00% 8.25E-02 0.01% 0.90% 3.08E-02 0.01% 0.99% 1.26E-03 0.01% 0.99% 1.56E-01 0.14% 0.90% 2.79E-02 0.01% 1.00% 3.97E+01 0.08% 0.90% 8.49E+00 0.08% 0.90% 2.76E+00 0.10% 100.00% 2.02E+03 0.00% 0.93% 1.80E+04 67.88% 67.96%
Secondary Solid Waste 4.38E+00 14.90% 15.18% 3.78E+03 0.01% 26.57% 0.00E+00 0.00% 0.00% 1.51E-06 0.00% 0.00% 5.07E-07 0.00% 0.00% 2.07E-08 0.00% 0.00% 1.91E-06 0.00% 0.00% 4.58E-07 0.00% 0.00% 1.89E-02 0.00% 0.00% 1.86E-02 0.00% 0.00% 0.00E+00 0.00% 0.00% 2.64E+01 0.00% 0.01% 1.37E+01 0.05% 0.05%
IDF Total 2.89E+01 98.16% 100.00% 1.42E+04 0.04% 100.00% 2.53E+00 0.46% 100.00% 9.18E+00 1.35% 100.00% 3.10E+00 1.31% 100.00% 1.26E-01 1.30% 100.00% 1.73E+01 15.07% 100.00% 2.80E+00 1.30% 100.00% 4.42E+03 8.94% 100.00% 9.44E+02 8.74% 100.00% 2.76E+00 0.10% 100.00% 2.18E+05 0.46% 100.00% 2.65E+04 99.89% 100.00%
Case 10B5 ILAW Glass 5.72E+00 19.44% 19.80% 7.77E+03 0.02% 55.76% 0.00E+00 0.00% 0.00% 8.35E+00 1.22% 98.94% 2.92E+00 1.23% 98.85% 1.20E-01 1.23% 98.85% 1.70E+01 14.81% 98.98% 2.66E+00 1.24% 98.85% 4.52E+03 9.15% 98.97% 9.62E+02 8.90% 98.97% 0.00E+00 0.00% 0.00% 1.74E+05 0.36% 98.90% 1.80E+04 67.82% 67.89%
LAW Melters 7.33E-03 0.02% 0.03% 9.86E+00 0.00% 0.07% 0.00E+00 0.00% 0.00% 1.40E-02 0.00% 0.17% 4.42E-03 0.00% 0.15% 1.80E-04 0.00% 0.15% 2.15E-02 0.02% 0.13% 4.02E-03 0.00% 0.15% 6.14E+00 0.01% 0.13% 1.30E+00 0.01% 0.13% 0.00E+00 0.00% 0.00% 2.27E+02 0.00% 0.13% 2.24E+01 0.08% 0.08%
ETF-Generated Secondary Solid Waste 1.88E+01 63.83% 64.99% 2.49E+03 0.01% 17.87% 2.40E+00 0.44% 100.00% 7.59E-02 0.01% 0.90% 2.95E-02 0.01% 1.00% 1.21E-03 0.01% 1.00% 1.55E-01 0.13% 0.90% 2.69E-02 0.01% 1.00% 4.11E+01 0.08% 0.90% 8.74E+00 0.08% 0.90% 3.92E+00 0.14% 100.00% 1.68E+03 0.00% 0.96% 8.47E+03 31.94% 31.98%
Secondary Solid Waste 4.38E+00 14.91% 15.18% 3.67E+03 0.01% 26.30% 0.00E+00 0.00% 0.00% 1.43E-06 0.00% 0.00% 4.92E-07 0.00% 0.00% 2.01E-08 0.00% 0.00% 1.90E-06 0.00% 0.00% 4.46E-07 0.00% 0.00% 1.76E-02 0.00% 0.00% 1.72E-02 0.00% 0.00% 0.00E+00 0.00% 0.00% 2.64E+01 0.00% 0.02% 1.12E+01 0.04% 0.04%
IDF Total 2.89E+01 98.20% 100.00% 1.39E+04 0.04% 100.00% 2.40E+00 0.44% 100.00% 8.44E+00 1.24% 100.00% 2.96E+00 1.25% 100.00% 1.21E-01 1.25% 100.00% 1.72E+01 14.96% 100.00% 2.69E+00 1.25% 100.00% 4.57E+03 9.25% 100.00% 9.72E+02 9.00% 100.00% 3.92E+00 0.14% 100.00% 1.75E+05 0.37% 100.00% 2.65E+04 99.89% 100.00%
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Table 9-2. Summary of Chemical Constituent Inventories and Waste Form Distributions Resulting from Hanford Tank
Waste Operations Simulator Runs.
1 SVF-4092, “IDF PA Case 7 - Current Information Case - Mass Balance, MMR-50049.” 2 SVF-4094, “IDF PA Case 8B - Tc_Tc-99 Removal from LAW Vitrification Off-Gas Condensate - Mass Balance, MMR-50051.”
3 SVF-4095, “IDF PA Case 9 - Removal of LAWPS - Mass Balance, MMR-50052.”
4 SVF-4096, “IDF PA Case 10A - Single Pass Tc_Tc-99 Retention in ILAW Glass of 32% - Mass Balance, MMR-50053.”
5 SVF-4097, “IDF PA Case 10B - Recycle Pass Tc_Tc-99 Retention in ILAW Glass of 68% - Mass Balance, MMR-50054.”
BBI = Best-Basis Inventory HTWOS = Hanford Tank Waste Operations Simulator ILAW = Immobilized Low-Activity Waste NA = not applicable
ETF = Effluent Treatment Facility IDF = Integrated Disposal Facility LAW = Low-Activity Waste
HTWOS Run Case Constituent Cr Hg NO3- Pb U
HTWOS BBI Inventory 5.91E+05 1.99E+03 5.60E+07 8.20E+04 6.45E+05
Units Kg %BBI %IDF Kg %BBI %IDF Kg %BBI %IDF Kg %BBI %IDF Kg %BBI %IDF
Case 71 ILAW Glass 4.90E+05 82.94% 99.70% 0.00E+00 0.00% 0.00% 0.00E+00 0.00% 0.00% 7.01E+04 85.44% 88.72% 8.10E+03 1.26% 99.76%
LAW Melters 7.44E+02 0.13% 0.15% 0.00E+00 0.00% 0.00% 0.00E+00 0.00% 0.00% 7.59E+01 0.09% 0.10% 1.15E+01 0.00% 0.14%
ETF-Generated Secondary Solid Waste 4.30E+00 0.00% 0.00% 9.58E+02 48.16% 48.89% 1.64E+05 0.29% 100.00% 8.82E+03 10.76% 11.17% 8.32E+00 0.00% 0.10%
Secondary Solid Waste 7.43E+02 0.13% 0.15% 1.00E+03 50.35% 51.11% 0.00E+00 0.00% 0.00% 1.19E+01 0.01% 0.02% 1.39E-03 0.00% 0.00%
IDF Total 4.92E+05 83.19% 100.00% 1.96E+03 98.51% 100.00% 1.64E+05 0.29% 100.00% 7.90E+04 96.30% 100.00% 8.12E+03 1.26% 100.00%
Case 8B2 ILAW Glass 4.93E+05 83.40% 99.73% 0.00E+00 0.00% 0.00% 0.00E+00 0.00% 0.00% 6.92E+04 84.42% 87.75% 7.99E+03 1.24% 99.79%
LAW Melters 5.73E+02 0.10% 0.12% 0.00E+00 0.00% 0.00% 0.00E+00 0.00% 0.00% 7.02E+01 0.09% 0.09% 8.81E+00 0.00% 0.11%
ETF-Generated Secondary Solid Waste 4.34E+00 0.00% 0.00% 9.50E+02 47.73% 48.45% 1.64E+05 0.29% 100.00% 9.58E+03 11.68% 12.14% 8.31E+00 0.00% 0.10%
Secondary Solid Waste 7.46E+02 0.13% 0.15% 1.01E+03 50.77% 51.55% 0.00E+00 0.00% 0.00% 1.18E+01 0.01% 0.01% 1.38E-03 0.00% 0.00%
Accumulator NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
IDF Total 4.94E+05 83.62% 100.00% 1.96E+03 98.50% 100.00% 1.64E+05 0.29% 100.00% 7.89E+04 96.20% 100.00% 8.01E+03 1.24% 100.00%
Case 93 ILAW Glass 4.95E+05 83.69% 99.72% 0.00E+00 0.00% 0.00% 0.00E+00 0.00% 0.00% 7.02E+04 85.61% 88.96% 7.94E+03 1.23% 99.76%
LAW Melters 6.61E+02 0.11% 0.13% 0.00E+00 0.00% 0.00% 0.00E+00 0.00% 0.00% 8.32E+01 0.10% 0.11% 1.05E+01 0.00% 0.13%
ETF-Generated Secondary Solid Waste 3.90E+00 0.00% 0.00% 9.14E+02 45.92% 46.64% 1.64E+05 0.29% 100.00% 8.62E+03 10.51% 10.92% 8.31E+00 0.00% 0.10%
Secondary Solid Waste 7.46E+02 0.13% 0.15% 1.05E+03 52.53% 53.36% 0.00E+00 0.00% 0.00% 1.18E+01 0.01% 0.02% 1.38E-03 0.00% 0.00%
IDF Total 4.96E+05 83.93% 100.00% 1.96E+03 98.45% 100.00% 1.64E+05 0.29% 100.00% 7.89E+04 96.24% 100.00% 7.96E+03 1.23% 100.00%
Case 10A4 ILAW Glass 4.60E+05 77.77% 92.77% 0.00E+00 0.00% 0.00% 0.00E+00 0.00% 0.00% 7.08E+04 86.39% 89.77% 8.30E+03 1.29% 98.87%
LAW Melters 6.54E+02 0.11% 0.13% 0.00E+00 0.00% 0.00% 0.00E+00 0.00% 0.00% 9.95E+01 0.12% 0.13% 1.15E+01 0.00% 0.14%
ETF-Generated Secondary Solid Waste 3.45E+04 5.83% 6.95% 1.64E+03 82.50% 83.61% 2.22E+06 3.97% 100.00% 7.97E+03 9.71% 10.09% 8.37E+01 0.01% 1.00%
Secondary Solid Waste 6.92E+02 0.12% 0.14% 3.22E+02 16.17% 16.39% 0.00E+00 0.00% 0.00% 1.23E+01 0.02% 0.02% 1.37E-03 0.00% 0.00%
IDF Total 4.95E+05 83.82% 100.00% 1.96E+03 98.68% 100.00% 2.22E+06 3.97% 100.00% 7.89E+04 96.24% 100.00% 8.39E+03 1.30% 100.00%
Case 10B5 ILAW Glass 4.62E+05 78.10% 92.78% 0.00E+00 0.00% 0.00% 0.00E+00 0.00% 0.00% 7.17E+04 87.43% 90.77% 7.97E+03 1.24% 98.85%
LAW Melters 6.41E+02 0.11% 0.13% 0.00E+00 0.00% 0.00% 0.00E+00 0.00% 0.00% 9.57E+01 0.12% 0.12% 1.20E+01 0.00% 0.15%
ETF-Generated Secondary Solid Waste 3.46E+04 5.85% 6.95% 1.65E+03 83.07% 83.60% 2.23E+06 3.98% 100.00% 7.18E+03 8.76% 9.09% 8.07E+01 0.01% 1.00%
Secondary Solid Waste 6.94E+02 0.12% 0.14% 3.24E+02 16.30% 16.40% 0.00E+00 0.00% 0.00% 1.25E+01 0.02% 0.02% 1.34E-03 0.00% 0.00%
IDF Total 4.98E+05 84.18% 100.00% 1.98E+03 99.37% 100.00% 2.23E+06 3.98% 100.00% 7.90E+04 96.32% 100.00% 8.06E+03 1.25% 100.00%
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Table 9-3. Tank Closure Alternative 2A Radioactive Constituents of Potential Concern Balance.
Table 7-3. Tank Closure Alternative 2A Radioactive Constituents of Potential Concern Balance
Iodine-129 Cesium-137 Carbon-14 Hydrogen-3
(Tritium) Uranium-233,
-234, -235, -238 Neptunium-237 Plutonium -239, -240 Strontium-90 Technetium-99
Best-Basis Inventory
Curies
% of BBI Curies
% of BBI Curies
% of BBI Curies
% of BBI Curies
% of BBI Curies
% of BBI Curies
% of BBI Curies
% of BBI Curies
% of BBI
BBIa 4.82×101
N/A 4.58×107
N/A 3.12×103
N/A 1.21×104
N/A 9.38×102
N/A 1.41×102
N/A 8.14×104
N/A 5.05×107
N/A 2.97×104
N/A
Tank Closure Waste Inventory
Tank residual wasteb 4.82×10-1
1.0 4.58×105
1.0 3.12×101
1.0 1.21×102
1.0 9.38 1.0 1.41 1.0 8.14×102
1.0 5.05×105
1.0 2.97×102
1.0
IHLW glassc 6.99×10-3
0.0 4.49×107
97.9 0 0.0 0 0.0 8.73×102
93.1 1.40×102
99.0 8.06×104
99.0 4.93×107
97.6 2.47×102
0.8
ILAW glass and retired LAW melters
ETF-generated solid
secondary wasted
9.56 19.8 4.45×105
1.0 0 0.0 0 0.0 5.47×101
5.8 8.35×10-3
0.0 1.45 0.0 2.30×103
0.0 2.88×104
96.9
3.36×10
1 69.7 4.59×10
-1 0.0 8.51 0.3 0 0.0 4.03×10
-2 0.0 5.11×10
-20.0 6.90×10
-4 0.0 6.42 0.0 8.63×10
1 0.3
Solid secondary wastee 4.65 9.7 1.95×105
0.4 0 0.0 0 0.0 3.64 0.4 2.83×10-1
0.2 1.98×102
0.2 7.76×105
1.5 4.31×102
1.5
Totalf 4.83×101 100.2 4.60×107 100.2 3.97×101 1.3 1.21×102 1.0 9.41×102 100.3 1.41×102 100.2 8.16×104 100.2 5.06×107 100.1 2.99×104 100.5
O ther Inventory
Solid and liquid secondary
waste from cesium and strontium capsules
Cesium and strontium
capsulesg
Air Emissions
0 N/A 1.99×105
N/A 0 N/A 0 N/A 0 N/A 0 N/A 0 N/A 3.16×105
N/A 0 N/A
0 N/A 4.59×10
7 N/A 0 N/A 0 N/A 0 N/A 0 N/A 0 N/A 1.98×10
7 N/A 0 N/A
Treatment air emissionsh 4.78×101
N/A 4.69×104
N/A 3.10×103
N/A 1.20×104
N/A 4.65×10-1
N/A NR N/A 4.04×101
N/A 3.55×104
N/A 1.47×101
N/A
a Source of BBI data is Inventory and Source Term Data Package, DOE-ORP-2003-02, Rev. 0 (DOE 2003a). b Represents 99.0 percent retrieval. For analysis purposes, waste inventories from tank waste retrieval leaks and ancillary equipment were assumed to be treated in the Waste Treatment Plant. c
To be stored on site until disposition decisions are made and implemented. This inventory would include the retired HLW melters. d Includes secondary liquids that would be sent to the ETF and treated; solids would be disposed of in an Integrated Disposal Facility. Excludes liquid secondary waste from the processing of cesium and
strontium capsules, which would be reported separately. e Includes solid low-level radioactive waste and mixed low-level radioactive waste streams that would be generated by the waste treatment operations. Such waste streams would include debris waste,
melter consumables, failed process components, analytical laboratory waste, spent resins, spent carbon adsorbent, high-efficiency particulate air filters, and other process-related waste. f Totals may exceed 100 percent due to conservative estimates or rounded numbers. BBI percentages were rounded to the nearest tenth. Carbon-14 and hydrogen-3 (tritium) may not total 100 percent; a
portion of each would be released to the offgas streams and stack, and a portion (ETF-generated liquid) would be disposed of in the State-Approved Land Disposal Site. g To be treated in the Waste Treatment Plant, resulting in glass waste, which would be stored on site until disposition decisions are made and implemented. h Includes air emissions from all waste treatment processes, including those from treatment of the cesium and strontium capsules. For analysis purposes, both iodine-129 capture and air emission releases
were assumed. Key: %=percent; BBI=Best-Basis Inventory; ETF=Effluent Treatment Facility; HLW=high-level radioactive waste; IHLW=immobilized high-level radioactive waste; ILAW=immobilized low-activity
waste; LAW=low-activity waste; N/A=not applicable; NR=not reported.
Source: SAIC 2011.
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Table 9-4. Tank Closure Alternative 2A Chemical Constituents of Potential Concern Balance.
Table 7-4. Tank Closure Alternative 2A Chemical Constituents of Potential Concern Balance
Chromium Mercury Nitrate Lead Total Uranium Acetonitrile Benzene Butanol PCBs 2,4,6-TCP
Kg
Best-Basis Inventory
% of
BBI Kg
% of
BBI Kg
% of
BBI Kg
% of
BBI Kg
% of
BBI Kg
% of
BBI Kg
% of
BBI Kg
% of
BBI Kg
% of
BBI Kg
% of
BBI
BBIa 5.98×105
N/A 1.83×103
N/A 7.08×107
N/A 8.41×104
N/A 5.97×105
N/A 2.95×104
N/A 2.40 N/A 3.45×106
N/A 1.68×103
N/A 1.11 N/A
Tank Closure Waste Inventory
Tank residual wasteb
5.98×103 1.0 1.83×101 1.0 7.08×105 1.0 8.41×102 1.0 5.97×103 1.0 2.95×102 1.0 2.40×10-2 1.0 3.45×104 1.0 1.68×101 1.0 1.11×10-2 1.0
IHLW glassc 1.36×105 22.7 0 0.0 0 0.0 7.45×104 88.6 5.52×105 92.5 0 0.0 0 0.0 0 0.0 0 0.0 0 0.0
ILAW glass and retired LAW melters
ETF- generated
solid secondary
wasted
Solid
secondary
wastee
4.56×105
76.2 0 0.0 0 0.0 8.88×103
10.6 3.74×104
6.3 0 0.0 0 0.0 0 0.0 0 0.0 0 0.0
4.43×101 0.0 5.55 0.3 9.01×106 12.7 4.58 0.0 4.00×101 0.0 NR N/A NR N/A NR N/A NR N/A NR N/A
1.94×103 0.3 1.76×103 96.4 0 0.0 2.47×102 0.3 2.32×103 0.4 NR N/A NR N/A NR N/A NR N/A NR N/A
Totalf 6.00×105 100.3 1.78×103 97.7 9.72×106 13.7 8.45×104 100.5 5.98×105 100.2 2.95×102 1.0 2.40×10-2 1.0 3.45×104 1.0 1.68×101 1.0 1.11×10-2 1.0
O ther Inventoryg
T reatment air
emissionsh
NR N/A 1.81×103 N/A NR N/A NR N/A NR N/A NR N/A 7.40×102 N/A NR N/A NR N/A NR N/A
a Source of BBI data is Inventory and Source Term Data Package, DOE-ORP-2003-02, Rev. 0 (DOE 2003a). b Represents 99.0 percent retrieval. For analysis purposes, waste inventories from tank waste retrieval leaks and ancillary equipment were assumed to be treated in the Waste Treatment Plant. c
Includes retired HLW melter inventory. IHLW glass would be stored on site until disposition decisions are made and implemented. d Includes secondary liquids that would be sent to the ETF and treated; solids would be disposed of in an Integrated Disposal Facility. e Includes solid low-level radioactive waste and mixed low-level radioactive waste streams that would be generated by the waste treatment operations. Such waste streams would include deb ris waste,
melter consumables, failed process components, analytical laboratory waste, spent resins, spent carbon adsorbent, high -efficiency particulate air filters, and other process-related waste. Excludes contaminated liquid effluent waste streams that would be treated at the ETF.
f Totals may exceed 100 percent due to conservative estimates or rounded numbers. BBI percentages were rounded to the nearest tenth. The organic chemicals (acetonitrile, benzene, butanol, PCBs,
and 2,4,6-TCP) may not total 100 percent because they would be destroyed during the thermal treatment processes. Nitrate may not total 10 0 percent because it would be volatilized and released through the facility stack.
g No chemical constituents of potential concern have been reported in the cesium and strontium capsule secondary-waste streams. h Includes air emissions from all waste treatment processes, including those from treatment of the cesium and strontium capsules. For analysis purposes, both mercury capture and air emission releases
were assumed. Note: To convert kilograms to pounds, multiply by 2.2046.
Key: %=percent; BBI=Best-Basis Inventory; butanol=n-butyl alcohol; ETF=Effluent Treatment Facility; HLW=high-level radioactive waste; IHLW=immobilized high-level radioactive waste; ILAW=immobilized low-activity waste; Kg=kilograms; LAW=low-activity waste; N/A=not applicable; NR=not reported; PCB=polychlorinated biphenyl; TCP=trichlorophenol.
Source: SAIC 2011.
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This selection of HTWOS run cases was designed to demonstrate the effects that slightly
different process flowsheet assumptions have on the distribution of 99Tc and 129I in the glass
versus non-glass waste forms. Some notable patterns observed include:
99Tc and 129I variations in glass waste form
Recovery of 99Tc from SBS-WESP liquid off-gas stream has significant influence on the
amount going to glass
Effect of single-pass/low and medium efficiency retention
Glass retention
Effect of LAWPS.
Overall this inventory data package maintains mass balance. Note that the inventories shown
address only the portion that is disposed of at the IDF. For each run case, the remainder
(e.g., HLW) will be disposed of offsite at a geologic repository.
9.1.1 Iodine-129 Variations (Figure 9-1 and Figure 9-2)
The HTWOS runs show that depending upon the run case, the 129I content in ILAW glass can
vary significantly from 20% to 56%. The higher retentions shown in Cases 7, 8B, and 9
demonstrate the efficiencies of recycle back to pretreatment versus Cases 10A and 10B which
are modeled in HTWOS using single-pass configuration to achieve 20% retention of 129I
retention in ILAW glass (similar to the TC&WM EIS case).
Comparing Case 7 (WTP with initial recycle from LAW Vitrification back to tank farms) to
Case 9 (WTP with recycle from LAW Vitrification to WTP Pretreatment) shows some very
slight difference, but overall these recycle configurations have no effect on the 129I retention in
ILAW glass.
Cases 10A and 10B show a significant amount of 129I going to ETF-generated SSW (~64%)
demonstrating the effects of HTWOS partitioning using a single-pass configuration versus
recycle (Case 7, 8B, and 9). Although the retention of 129I in ILAW glass was fixed at 20%,
most of the remainder ends up in ETF-generated SSW and about 15% is reported to WTP SSW.
The converse of this is demonstrated for the recycle cases 7, 8B, and 9, where about 56% of the 129I ends up in ILAW glass, and most of the remainder (~41%) ends up in WTP SSW, not
ETF-generated SSW. This is a result of the manner in which HTWOS treats the off-gas waste
streams under recycle conditions. Basically, the inventory that does not end up in the glass
accumulates in the carbon absorber beds and HLW silver mordenite media which is disposed of
as SSW.
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Figure 9-1. Iodine-129 Distributions in Integrated Disposal Facility Waste Forms.
EIS = Environmental Impact Statement IDF = Integrated Disposal Facility SSW = Secondary Solid Waste
ETF = Effluent Treatment Facility ILAW = Immobilized Low-Activity Waste WTP = Waste Treatment and Immobilization Plant
0.00%
10.00%
20.00%
30.00%
40.00%
50.00%
60.00%
70.00%
80.00%
90.00%
100.00%
Case7
Case8B
Case9
Case10A
Case10B
EIS Case7
Case8B
Case9
Case10A
Case10B
EIS Case7
Case8B
Case9
Case10A
Case10B
EIS
ILAW glass ETF Generated Secondary SolidWaste
WTP SSW
I-129 Distributions in IDF Waste Forms
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Figure 9-2. Iodine-129 Inventory in Integrated Disposal Facility Waste Forms.
EIS = Environmental Impact Statement IDF = Integrated Disposal Facility SSW = Secondary Solid Waste
ETF = Effluent Treatment Facility ILAW = Immobilized Low-Activity Waste WTP = Waste Treatment and Immobilization Plant
0.00E+00
5.00E+00
1.00E+01
1.50E+01
2.00E+01
2.50E+01
3.00E+01
3.50E+01
Case7
Case8B
Case9
Case10A
Case10B
EIS Case7
Case8B
Case9
Case10A
Case10B
EIS Case7
Case8B
Case9
Case10A
Case10B
EIS
ILAW Glass ETF Generated Secondary Solid Waste WTP SSW
Cu
rie
s
I-129 Inventory in IDF Waste Forms
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Similar to the ILAW glass results, the ETF-generated SSW and WTP SSW results show that
recycling from LAW Vitrification to tank farms or to WTP Pretreatment has no effect on the
distribution of 129I in glass versus grout and that these distributions are mainly based on the
effects of recycle and glass retention fractions implemented in HTWOS (e.g., 20%, 56% with
recycle).
9.1.2 Technetium-99 Variations (Figure 9-3 and Figure 9-4)
The HTWOS runs show variations in the 99Tc retention in ILAW glass ranging from 32% to
99%.
Case 7 (with LAWPS) and Case 9 (without LAWPS) show negligible differences. Both cases
include recycle; therefore, operation of LAWPS versus WTP Pretreatment has no effect on 99Tc
retention in ILAW glass. Case 8B shows a significant decrease of 99Tc retention in ILAW glass
compared to Case 7 and Case 9 by approximately 61%. Case 8B removes 99% of the 99Tc from
the off-gas liquid recycle stream; therefore, Case 8B (although it includes recycle) is effectively
the same as a single-pass configuration.
Cases 10A and 10B use a single-pass configuration with 99Tc retention in glass fixed at 32% and
68% respectively. Cases 10A and 10B were contrived scenarios developed to test the limits of
non-glass waste form concentrations that IDF could receive and still meet the performance
criteria for the facility. These cases are included to help establish waste acceptance criteria for
specific waste forms. Previous studies at VSL indicate a 32% 99Tc retention in ILAW glass for
single pass and 68% retention with recycle when averaged across all LAW feed types tested.
These HTWOS runs demonstrate a modest range of 99Tc retention in glass, which may not be as
high as what was analyzed in the TC&WM EIS or in previous HTWOS flowsheet runs (>90%).
As shown by the ETF-generated secondary solids and secondary solids results for single pass
(Cases 10A and 10B), most of the 99Tc that does not end up in ILAW glass ends up in
ETF-generated secondary solids with only a small amount (<1%) going to SSW.
Although Case 8B (99% removal of 99Tc from LAW off-gas) effectively represents a single pass,
HTWOS separates and accounts for this 99Tc in the “Accumulator”; therefore, it is not present in
ETF-generated SSW or SSW. The 99Tc inventory in the “Accumulator” at the end of the WTP
mission is 16,500 Ci. For analysis purposes, this inventory will not be disposed of at the IDF
and will likely be disposed of offsite or in IHLW glass.
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Figure 9-3. Technetium-99 Distributions in Integrated Disposal Facility Waste Forms.
EIS = Environmental Impact Statement IDF = Integrated Disposal Facility SSW = Secondary Solid Waste
ETF = Effluent Treatment Facility ILAW = Immobilized Low-Activity Waste WTP = Waste Treatment and Immobilization Plant
0.00%
10.00%
20.00%
30.00%
40.00%
50.00%
60.00%
70.00%
80.00%
90.00%
100.00%
Case 7 Case8B
Case 9 Case10A
Case10B
EIS Case 7 Case8B
Case 9 Case10A
Case10B
EIS Case 7 Case8B
Case 9 Case10A
Case10B
EIS
ILAW glass ETF Generated Secondary Solid Waste WTP SSW
Tc-99 Distributions in IDF Waste Forms
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Figure 9-4. Technetium-99 Inventory in Integrated Disposal Facility Waste Forms.
EIS = Environmental Impact Statement IDF = Integrated Disposal Facility SSW = Secondary Solid Waste
ETF = Effluent Treatment Facility ILAW = Immobilized Low-Activity Waste WTP = Waste Treatment and Immobilization Plant
0.00E+00
5.00E+03
1.00E+04
1.50E+04
2.00E+04
2.50E+04
3.00E+04
Case7
Case8B
Case9
Case10A
Case10B
EIS Case7
Case8B
Case9
Case10A
Case10B
EIS Case7
Case8B
Case9
Case10A
Case10B
EIS
ILAW Glass ETF Generated Secondary Solid Waste WTP SSW
Cu
rie
sTc-99 Inventory in IDF Waste Forms
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10.0 DATA QUALITY ASSURANCE FOR THE INTEGRATED DISPOSAL FACILITY
INVENTORY DATA PACKAGE
The source data used to develop inventories for the 2017 IDF PA will come directly from
existing sources such as the Best-Basis Inventory (TWINS), HTWOS, and the TC&WM EIS,
and through literature reviews of project-approved technical documents.
No new data will be developed and no calculations will be performed. Each of these sources has
already established compliance with ASME NQA-1-2008, “Quality Assurance Requirements for
Nuclear Facility Applications (QA)” and NQA-1a-2009, “Quality Assurance Requirements for
Nuclear Facility Applications Addenda,” Quality Assurance requirements as presented in
Table 10-1 below.
Table 10-1. Source Data Quality Assurance.
Data Source Required Quality Assurance
Best-Basis Inventory RPP-RPT-58911, Rev. 11, “Tank Waste Information Network System
Quality Assurance Plan.”
Hanford Tank Waste Operations
Simulator
RPP-50816, Rev. 1, “Software Management Plan for Grade D Custom
Developed Hanford Tank Waste Operations Simulator (HTWOS).”
Tank Closure and Waste
Management Environmental Impact
Statement (TC&WM EIS)
A Quality Assurance review by the U.S. Department of Energy (DOE)
was completed in November 2008 to ensure that the TC&WM EIS
Quality Assurance Plan was compliant with:
DOE O 414.C, Quality Assurance
DOE O 451.1B, National Environmental Policy Act Compliance Program
“NEPA Contracting Reform Guidance” (DOE 1996)
DOE P 226.1, Department of Energy Oversight Policy
DOE P 251.1A, Departmental Directives Program Policy
For the IDF PA Inventory Data Package, spreadsheets will be extracted from TWINS and
HTWOS for data presentation purposes. According to TFC-ENG-DESIGN-C-32, “Utility
Calculation Software Management,” spreadsheets exempted from the requirements of this
procedure include:
Spreadsheets that do not perform calculations or do not perform technical data
manipulation
Spreadsheets that are used for administrative type activities (such as table generation)
Spreadsheets that are generated as a result of a query or download from TWINS or other
system registered on the Hanford Information Network System, provided that nothing is
done to modify the data.
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The data quality assurance for all data used as the basis of the inventory estimates in the IDF PA
Inventory Data Package will be consistent with quality assurance requirements presented in
Table 10-1 and with the spreadsheet exemptions included in TFC-ENG-DESIGN-C-32.
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11.0 REFERENCES
40 CFR 268.40, “Applicability of Treatment,” Code of Federal Regulations, as amended.
40 CFR 268.45, “Treatment Standards for Hazardous Debris,” Code of Federal Regulations, as
amended.
62 FR 8693, 1997, “Record of Decision for the Tank Waste Remediation System, Hanford Site,
Richland, WA,” Federal Register, Vol. 62, pp. 8693–8704 (February 26).
78 FR 75913, 2013, “Record of Decision: Final Tank Closure and Waste Management
Environmental Impact Statement for the Hanford Site, Richland, Washington,” Federal
Register, Vol. 78, pp. 75913–75919 (December 13).
24590-LAW-MOD-LMP-00002, “Data Sheet Low Activity Waste Melter 2,” Rev. 1, River
Protection Project Waste Treatment Plant, Richland, Washington.
24590-WTP-PENG-14-0006, 2015, “Secondary Wastes Compliance Plan,” Rev. 1, River
Protection Project Waste Treatment Plant, Richland, Washington.
24590-WTP-RPT-ENS-10-009, 2010, “Secondary Waste Estimates for WTP HVAC HEPA
Filters,” Rev. 0, River Protection Project Waste Treatment Plant, Richland, Washington.
24590-WTP-RPT-ENS-10-010, 2010, “WTP Estimate of Secondary Radioactive Solid Waste
Generation,” Rev. 0, River Protection Project Waste Treatment Plant, Richland,
Washington.
24590-WTP-RPT-PT-02-005, 2013, “Flowsheet Bases, Assumptions, and Requirements,”
Rev. 7, Bechtel National, Inc., Richland, Washington.
9404636B R2, 1994, “Request for Office of Waste Management Integrated Data Base
High-Level Waste Data Information Update” (letter from R. W. Powell to L. Erickson,
U.S. Department of Energy, Richland Operations Office, November 4), Westinghouse
Hanford Company, Richland, Washington.
ASME NQA-1-2008, 2008, “Quality Assurance Requirements for Nuclear Facility Applications
(QA)”, ASME International, New York, New York.
ASME NQA-1a-2009, 2009, “Quality Assurance Requirements for Nuclear Facility Applications
Addenda,” ASME International, New York, New York.
Comprehensive Environmental Response, Compensation, and Liability Act of 1980, Public
Law 96-510, 94 Stat. 2767, 42 USC 9601 et seq.
DOE, 1996, “NEPA Contracting Reform Guidance,” U.S. Department of Energy, Office of
NEPA Policy and Assistance, Washington, D.C.
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DOE/EIS-0189, 1996, “Tank Waste Remediation System, Hanford Site, Richland, Washington,
Final Environmental Impact Statement,” U.S. Department of Energy and Washington
State Department of Ecology, Richland, Washington.
DOE/EA-01386, 2009, “Final Environmental Assessment for the Remote-Handled Waste
Disposition Project,” U.S. Department of Energy Idaho Operations Office, Idaho Falls,
Idaho.
DOE/EIS-0391, 2012, “Final Tank Closure and Waste Management Environmental Impact
Statement for the Hanford Site, Richland, Washington,” U.S. Department of Energy,
Office of River Protection, Richland, Washington.
DOE O 414.1C, 2005, Quality Assurance, U.S. Department of Energy, Washington, D.C.
DOE O 451.1B, 2000, National Environmental Policy Act Compliance Program,
U.S. Department of Energy, Washington, D.C.
DOE/ORP-2003-02, 2003, Environmental Impact Statement for Retrieval, Treatment, and
Disposal of Tank Waste and Closure of Single-Shell Tanks at the Hanford Site, Richland
WA Inventory and Source Term Data Package, Rev. 0, U.S. Department of Energy,
Office of River Protection, Richland, Washington.
DOE P 226.1, 2006, Department of Energy Oversight Policy, U.S. Department of Energy,
Washington, D.C.
DOE P 251.1A, 2006, Departmental Directives Program Policy, U.S. Department of Energy,
Washington, D.C.
Grondin, R. 02-18-2016, “waste streams slated for offsite,” (e-mail to R. L. Keller), Washington
River Protection Solutions LLC (WRPS), Richland, Washington.
HNF-3273, 1998, “Hanford Defined Waste Model Limitations and Improvements,” Rev. 0A,
Lockheed Martin Hanford Corporation/Cogema, Richland, Washington.
HNF-4921, 1999, “Immobilized Low-Activity Tank Waste Inventory Data Package,” Rev. 0,
Fluor Daniel Northwest, Inc., Richland, Washington.
HNF-58821, 2015, “Effluent Treatment Facility Mass Balance Calculation for DFLAW
Mission,” Rev. 0, CH2M, Richland, Washington.
HNF-EP-0918, 2014, “Solid Waste Integrated Forecast Technical (SWIFT) Report FY2014 -
FY2050, 2014.0,” Rev. 24, CH2M HILL Plateau Remediation Company, Richland,
Washington.
HNF-SD-WM-SP-012, 1997, “Tank Waste Remediation System Operation and Utilization
Plan,” Rev. 0, Numatec Hanford Corporation, Richland, Washington.
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HNF-SD-WM-SP-012, 1999, “Tank Waste Remediation System Operation and Utilization
Plan,” Rev. 1, Numatec Hanford Corporation, Richland, Washington.
HNF-SD-WM-SP-012, 2000, “Tank Farm Contractor Operation and Utilization Plan,” Rev. 2,
CH2M HILL Hanford Group, Inc., Richland, Washington.
HNF-SD-WM-SP-012, 2001, “Tank Farm Contractor Operation and Utilization Plan,” Rev. 3,
Numatec Hanford Corporation/CH2M HILL Hanford Group, Inc., Richland, Washington.
HNF-SD-WM-SP-012, 2003, “Tank Farm Contractor Operation and Utilization Plan,” Rev. 4B,
CH2M HILL Hanford Group, Inc., Richland, Washington.
HNF-SD-WM-SP-012, 2003, “Tank Farm Contractor Operation and Utilization Plan,” Rev. 5A,
CH2M HILL Hanford Group, Inc., Richland, Washington.
HNF-SD-WM-TI-740, 1999, “Standard Inventories of Chemicals and Radionuclides in Hanford
Site Tank Wastes,” Rev. 0, Lockheed Martin Hanford Corporation, Richland,
Washington.
LA-UR-96-3860, 1997, “Hanford Tank Chemical and Radionuclide Inventories: HDW Model
Rev. 4,” Los Alamos National Laboratory, Los Alamos, New Mexico.
ORNL/TM-7175, 1980, “A User’s Manual for the ORIGEN2 Computer Code,” Chemical
Technology Division, Oak Ridge National Laboratory, Oak Ridge, Tennessee.
ORNL, 1990, “Performance Testing of Grout-Based Waste Forms for the Solidification of Anion
Exchange Resins,” Chemical Technology Division, Oak Ridge National Laboratory, Oak
Ridge, Tennessee.
ORP-11242, 2008, “River Protection Project System Plan,” Rev. 3, U.S. Department of Energy,
Office of River Protection, Richland, Washington.
ORP-11242, 2011, “River Protection Project System Plan,” Rev. 6, U.S. Department of Energy,
Office of River Protection, Richland, Washington.
ORP-11242, 2014, “River Protection Project System Plan,” Rev. 7, U.S. Department of Energy,
Office of River Protection, Richland, Washington.
PNNL-19681, 2010, “Tc-99 Ion Exchange Resin Testing,” Pacific Northwest National
Laboratory, Richland, Washington.
PNNL-22747/SRNL-STI-2013-00465, 2013, “Supplemental Immobilization of Hanford
Low-Activity Waste: Cast Stone Screening Tests,” Pacific Northwest National
Laboratory/Savannah River National Laboratory, Richland, Washington.
Resource Conservation and Recovery Act of 1976, 42 USC 6901, et seq.
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RPP-7625, 2015, “Guidelines for Updating Best-Basis Inventory,” Rev. 12, Washington River
Protection Solutions, LLC, Richland, Washington.
RPP-10365, 2002, “Best-Basis Inventory Assessment Report,” Rev. 0, CH2M HILL Hanford
Group, Inc., Richland, Washington.
RPP-13489, 2002, “Activity of Fuel Batches Processed Through Hanford Separations Plants,
1944 through 1989,” Rev. 0, CH2M HILL Hanford Group, Inc., Richland, Washington.
RPP-17152, 2009, “Hanford Tank Waste Operations Simulator (HTWOS) Model Design
Description,” Rev. 1, Washington River Protection Solutions, LLC/AEM Consulting,
LLC, Richland, Washington.
RPP-17152, 2014, “Hanford Tank Waste Operations Simulator (HTWOS) Version 7.7 Model
Design Document,” Rev. 9, Washington River Protection Solutions, LLC/AEM
Consulting, LLC, Richland, Washington.
RPP-17152, 2015, “Hanford Tank Waste Operations Simulator (HTWOS) Version 8.1 Model
Design Document,” Rev. 12, Washington River Protection Solutions, LLC/AEM
Consulting, LLC, Richland, Washington.
RPP-19822, 2005, “Hanford Defined Waste Model – Revision 5.0,” Rev. 0-A, CH2M HILL
Hanford Group, Inc./Technical Resources International, Inc., Richland, Washington.
RPP-20692, 2004, “Inventory Data Package for the 2005 Integrated Disposal Facility
Performance Assessment,” Rev. 0, CH2M HILL Hanford Group, Inc., Richland,
Washington.
RPP-20692, 2005, “Inventory Data Package for the 2005 Integrated Disposal Facility
Performance Assessment,” Rev. 1, CH2M HILL Hanford Group, Inc., Richland,
Washington.
RPP-26781, 2015, “Tank Operations Contractor Sampling Projections for FY2016 through
FY2020,” Rev. 11, Washington River Protection Solutions, LLC, Richland, Washington.
RPP-33715, 2015, “Double-Shell and Single-Shell Tank Inventory Input to the Hanford Tank
Waste Operations Simulator Model – 2015-2 Update,” Rev. 9, Washington River
Protection Solutions, LLC, Richland, Washington.
RPP-50816, 2013, “Software Management Plan for Grade D Custom Developed Hanford Tank
Waste Operations Simulator (HTWOS),” Rev. 1, Washington River Protection
Solutions, LLC, Richland, Washington.
RPP-54130, 2012, “Technetium Retention in WTP LAW Glass with Recycle Flow-Sheet: DM10
Melter Testing, VSL-12R2640-1, Rev. 0,” Rev. 0, Vitreous State Laboratory, The
Catholic University of America/Energy Solutions, Federal EPC, Inc., Richland,
Washington.
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RPP-RPT-58204, 2014, “Spent/Failed Low-Activity Waste Melter Transport System Evaluation
Report,” Rev. 0, Washington River Protection Solutions, LLC/Lucas Engineering and
Management Services/Barnhart Crane and Rigging, Richland, Washington.
RPP-RPT-58911, 2015, “Tank Waste Information Network System Quality Assurance Plan,”
Rev. 11, Pacific Northwest National Laboratory, Richland, Washington.
RPP-SPEC-43722, 2013, “Secondary Liquid Waste Treatment Plant Project (T3W08) System
Specification,” Rev. 2, Washington River Protection Solutions, LLC, Richland,
Washington.
SD-WM-TI-057, 1993, “Preliminary Estimation of the Waste Inventories in Hanford Tanks
Through 1980,” Rev. 0-A, Westinghouse Hanford Company, Richland, Washington.
SVF-4092, 2015, “IDF PA Case 7 - Current Information Case - Mass Balance, MMR-50049,”
Rev. 0, Washington River Protection Solutions, LLC, Richland, Washington.
SVF-4094, 2015, “IDF PA Case 8B - Tc_Tc-99 Removal from LAW Vitrification Off-Gas
Condensate - Mass Balance, MMR-50051,” Rev. 0, Washington River Protection
Solutions, LLC, Richland, Washington.
SVF-4095, 2015, “IDF PA Case 9 - Removal of LAWPS - Mass Balance, MMR-50052,” Rev. 0,
Washington River Protection Solutions, LLC, Richland, Washington.
SVF-4096, 2015, “IDF PA Case 10A - Single Pass Tc_Tc-99 Retention in ILAW Glass of 32% -
Mass Balance, MMR-50053,” Rev. 0, Washington River Protection Solutions, LLC,
Richland, Washington.
SVF-4097, 2015, “IDF PA Case 10B – Recycle Pass Tc_Tc-99 Retention in ILAW Glass of
68% - Mass Balance, MMR-50054,” Rev. 0, Washington River Protection
Solutions, LLC, Richland, Washington.
TFC-ENG-DESIGN-C-32, “Utility Calculation Software Management,” Washington River
Protection Solutions LLC (WRPS) Tank Farms, Richland, Washington.
Tank Waste Information Network System (TWINS), Queried 09/22/2004, [Best-Basis Inventory,
Best-Basis Summary Report], http://twins.pnl.gov:8001/twins.htm.
VSL-13R2800-1, 2013, “Wet Electrostatic Precipitator Performance and Technetium-Rhenium
Behavior in LAW Recycle Flow-Sheet,” Rev. 0, Vitreous State Laboratory, The Catholic
University of America, Washington, D.C.
WHC-EP-0375, 1991, “Engineering Study for the Treatment of Spent Ion Exchange Resin
Resulting from Nuclear Process Applications,” Westinghouse Hanford Company,
Richland, Washington.
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WHC-SD-WM-RPT-164, 1995, “Inventories for Low-Level Waste Tank Waste,” Rev. 0,
Westinghouse Hanford Company, Richland, Washington.
WT-ST-042, 2010, “Curie Distribution for Alternatives 1, 2A, 2B, 3A, 3B, 3C, 4, 5, 6A, 6B, and
6C,” Rev. 10, Columbia Energy & Environmental Services, Inc., Richland, Washington.
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HTWOS INVENTORY TABLES
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APPENDIX A
HTWOS INVENTORY TABLES
This Appendix includes complete Best-Basis Inventory (BBI) tables for Hanford Tank Waste
Operations Simulator (HTWOS) Run Cases 7, 8B, 9, 10A, and 10B for each Integrated Disposal
Facility (IDF) waste stream (with all radionuclides decayed to 2008 and to 2051, which is the
assumed facility closure date for the IDF). Specifically, these IDF waste streams include:
Immobilized Low-Activity Waste glass
Low-Activity Waste melters
Effluent Treatment Facility -generated secondary solid waste
Secondary solid waste.
Note: HTWOS reports certain radionuclides (i.e., 227Ac, 228Ra, 93mNb) as negative inventory
values, which is due to the fact that HTWOS has four second-order decay chains; parent to
daughter to granddaughter isotope (see Section 2.7.7 in RPP-17152, Rev. 12, “Hanford Tank
Waste Operations Simulator (HTWOS) Version 8.1 Model Design Document”).
During the pretreatment and treatment processing, HTWOS partitions
parent/daughter/granddaughter radionuclides differently because the different isotopes have
different chemical behaviors. This results in a different ratio of parent to daughter to
granddaughter in each process stream than was observed in the original waste stream. When
HTWOS back-decays the radionuclides in each stream to the reference decay date, the different
amounts of parent/daughter/granddaughter isotopes can back-decay to different values (including
negative values) because they are present in different ratios.
None of the radionuclides reporting negative inventories are considered major risk drivers and
therefore will have a negligible impact on the overall performance of the IDF.
This Appendix also includes complete BBI tables for HTWOS Run Cases 7, 8B, 9, 10A, and
10B including more detailed Waste Treatment and Immobilization Plant (WTP) Secondary Solid
waste streams (with all radionuclides decayed to 2008 and to 2051, which is the assumed facility
closure date for the IDF). Each detailed waste stream inventory is reported in curies for
radionuclides and kilograms for chemicals. Specifically, these detailed WTP Secondary Solid
Waste streams include:
High Effluent Particulate Air (HEPA) filters
Ion Exchange resin
Low-Activity Waste and High-Level Waste carbon adsorber beds
High-Level Waste silver mordenite absorbent
Other debris.
The partition fractions used to distribute inventories to these more detailed waste streams were
based on simple ratios computed from information reported in Appendix C of
24590-WTP-RPT-ENS-10-010, “WTP Estimate of Secondary Radioactive Solid Waste
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Generation” and from Tables 3-15 through 3-26 of 24590-WTP-RPT-ENS-10-009, “Secondary
Waste Estimates for WTP HVAC HEPA Filters.” If a BBI constituent was not reported in either
of these source documents, it was listed as NR (not reported) in Section 4 of Tables A-1 through
A-10. Specifically, the list of NR constituents include:
106-Ru 226-Ra 232-Th 243-Cm Cs PO4-3 Y
113m-Cd 227-Ac 232-U 244-Cm Mo SO2
125-Sb 228-Ra 242-Cm 90-Y NO2- SO3
137m-Ba 229-Th 242-Pu 93-Zr NO3- SO4-2
151-Sm 231-Pa 243-Am 93m-Nb OH- TOC
A comparison of this list to the constituents of potential concern analyzed in DOE/EIS-0391,
“Final Tank Closure and Waste Management Environmental Impact Statement for the Hanford
Site, Richland, Washington” shows that nitrate is the only constituent of potential concern that is
NR. All run cases in the 2017 IDF Performance Assessment analysis report zero inventory for
nitrate in WTP Secondary Solid Waste.
REFERENCES
24590-WTP-RPT-ENS-10-009, 2010, “Secondary Waste Estimates for WTP HVAC HEPA
Filters,” Rev. 0, River Protection Project Waste Treatment Plant, Richland, Washington.
24590-WTP-RPT-ENS-10-010, 2010, “WTP Estimate of Secondary Radioactive Solid Waste
Generation,” Rev. 0, River Protection Project Waste Treatment Plant, Richland,
Washington.
DOE/EIS-0391, 2012, “Final Tank Closure and Waste Management Environmental Impact
Statement for the Hanford Site, Richland, Washington,” U.S. Department of Energy,
Office of River Protection, Richland, Washington.
RPP-17152, 2015, “Hanford Tank Waste Operations Simulator (HTWOS) Version 8.1 Model
Design Document,” Rev. 12, Washington River Protection Solutions, LLC/AEM
Consulting, LLC, Richland, Washington.
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Table A-1. Run Case 7 Radionuclides.
SVF-4092, IDF PA Case 7 - Current Information Case - Mass Balance, MMR-50049.xlsm
WASTE STREAM 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
LAW Glass Subtotal (IDF) 1.19E+01 3.30E+03 4.03E+03 3.87E+02 1.62E+01 2.03E-01 1.04E+04 9.86E+03 0.00E+00 2.15E-01 8.50E-05 8.63E-04 1.10E-03 9.21E-03 1.41E+01 2.93E+02 4.13E-08 8.25E-08 9.40E-08 1.42E-01 9.87E+00 2.98E+00 1.21E-01 9.43E-02 1.71E+01 2.28E+02 2.68E+00 4.41E+03 9.29E+02 6.04E+03 7.32E+03 1.21E+02 7.25E-02 3.05E+00 1.33E+01 2.94E+02 0.00E+00 4.94E+01 1.78E-04 4.43E+03 1.40E+02 2.52E+05 2.52E+05 7.76E-04 5.54E-04 2.59E+04
LAW Spent Melter Subtotal (IDF) 1.27E-02 5.19E+00 4.36E+00 4.42E-01 2.33E-02 2.84E-04 1.35E+01 1.27E+01 0.00E+00 2.98E-04 1.18E-07 1.20E-06 1.53E-06 1.13E-05 2.04E-02 4.04E-01 5.75E-11 1.15E-10 1.31E-10 1.82E-04 1.28E-02 4.22E-03 1.71E-04 1.30E-04 2.07E-02 3.40E-01 3.82E-03 5.84E+00 1.23E+00 7.87E+00 9.69E+00 1.34E-01 9.92E-05 4.45E-03 1.57E-02 3.46E-01 0.00E+00 8.89E-02 2.48E-07 7.94E+00 1.79E-01 3.14E+02 3.14E+02 1.08E-06 7.70E-07 3.68E+01
ETF Solid Waste Form to IDF 6.59E-03 1.24E+01 6.87E+01 1.66E+00 6.28E-02 1.17E-05 6.65E-01 6.28E-01 3.52E+00 1.66E-05 4.44E-10 2.06E-07 8.28E-08 1.80E-04 6.32E-02 7.28E+00 3.69E-15 7.47E-11 3.11E-17 2.97E-07 1.76E-05 2.87E-03 1.20E-04 3.35E-05 7.01E-05 3.14E-04 2.75E-03 6.08E-03 1.26E-03 2.05E-02 9.60E-03 4.26E-01 3.36E-04 1.05E-05 4.89E-02 1.08E+00 2.34E+00 1.28E-01 8.56E-05 1.14E+01 2.85E+00 9.64E+01 9.64E+01 2.03E-07 5.65E-03 2.25E-01
Solid Waste Forms from Treatment Processes (IDF) 6.28E-05 7.98E-03 1.30E-02 1.91E-02 1.19E+01 8.26E-02 3.97E+03 3.74E+03 0.00E+00 2.64E-03 6.64E-07 4.04E-05 2.02E-05 3.50E-08 1.58E-06 1.11E-03 1.19E-09 3.97E-09 5.54E-09 2.27E-08 1.64E-06 5.12E-07 2.08E-08 1.56E-08 1.99E-06 1.10E-02 4.61E-07 1.98E-02 1.95E-02 1.04E-02 8.81E-04 3.94E-04 8.70E-09 7.60E-07 6.74E-04 1.10E-03 0.00E+00 4.16E-04 1.68E-05 3.72E-02 5.40E-03 2.57E+01 2.57E+01 2.68E-04 -1.03E-03 1.96E+01
Non-IDF Stream -2.14E-03 5.04E+02 1.51E+00 1.58E-01 5.98E-01 7.11E+02 3.87E+07 3.65E+07 8.24E+02 3.15E+06 7.91E+02 4.82E+04 2.41E+04 1.18E-05 -9.32E+00 -2.89E+02 1.42E+00 4.73E+00 6.61E+00 8.17E+00 6.37E+02 2.14E+02 8.75E+00 6.05E+00 9.02E+01 2.25E+03 1.94E+02 4.30E+04 9.10E+03 1.42E+05 7.15E+04 8.22E-02 6.78E-01 6.38E+01 5.04E-03 1.07E-01 2.81E+03 1.41E+03 3.71E+03 1.26E+05 4.51E-02 4.27E+07 4.27E+07 3.37E+03 2.85E+03 2.14E+01
BBI 1.20E+01 3.89E+03 4.13E+03 3.91E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 5.51E+02 3.57E+06 9.07E+02 5.30E+04 2.55E+04 9.95E-03 4.14E+00 6.77E+00 1.48E+00 5.16E+00 6.77E+00 8.87E+00 6.82E+02 2.37E+02 9.71E+00 6.50E+00 1.15E+02 2.63E+03 2.15E+02 4.94E+04 1.08E+04 1.57E+05 8.38E+04 1.22E+02 8.26E-01 7.23E+01 1.35E+01 2.98E+02 2.82E+03 1.62E+03 4.10E+03 1.44E+05 1.44E+02 4.76E+07 4.76E+07 3.73E+03 3.17E+03 2.65E+04
HTWOS Feed 1.20E+01 3.89E+03 4.13E+03 3.91E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 8.28E+02 3.57E+06 9.07E+02 5.30E+04 2.55E+04 9.95E-03 4.14E+00 6.77E+00 1.48E+00 5.16E+00 6.77E+00 8.87E+00 6.82E+02 2.37E+02 9.71E+00 6.50E+00 1.15E+02 2.64E+03 2.16E+02 5.14E+04 1.09E+04 1.57E+05 8.39E+04 1.22E+02 8.27E-01 7.23E+01 1.35E+01 2.98E+02 2.82E+03 1.62E+03 4.10E+03 1.44E+05 1.44E+02 4.76E+07 4.76E+07 3.73E+03 3.17E+03 2.65E+04
HTWOS Feed Adjusted Minus TF and TRU Accumulation 1.20E+01 3.83E+03 4.11E+03 3.90E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 8.27E+02 3.27E+06 8.25E+02 4.95E+04 2.45E+04 9.43E-03 4.54E+00 9.40E+00 1.43E+00 4.83E+00 6.63E+00 8.39E+00 6.51E+02 2.19E+02 8.95E+00 6.20E+00 1.08E+02 2.51E+03 1.99E+02 4.82E+04 1.02E+04 1.50E+05 7.99E+04 1.21E+02 7.63E-01 6.79E+01 1.34E+01 2.96E+02 2.81E+03 1.48E+03 3.80E+03 1.33E+05 1.44E+02 4.40E+07 4.40E+07 3.49E+03 2.96E+03 2.65E+04
ACCUMULATION STREAM 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
PT-Accumulation 1.50E-04 2.35E+00 2.92E-01 3.78E-01 5.46E-02 1.56E+00 3.02E+05 2.85E+05 2.43E-01 1.09E+05 3.10E+01 1.20E+03 3.71E+02 4.22E-06 -3.48E-01 -6.49E+00 1.12E-02 9.46E-02 1.86E-02 6.92E-02 4.31E+00 1.63E+00 6.70E-02 5.05E-02 1.01E+00 2.88E+01 1.47E+00 7.15E+02 1.58E+02 1.84E+03 9.67E+02 8.90E-02 1.08E-02 9.65E-01 2.24E-02 5.00E-01 1.49E+00 2.51E+01 7.89E+01 2.23E+03 6.59E-02 8.98E+05 8.98E+05 1.10E+02 9.77E+01 2.52E+01
TF-Accumulation 7.47E-06 6.61E+01 2.11E+01 1.96E+00 7.59E-02 2.37E-02 1.64E+04 1.54E+04 2.11E-01 3.04E+05 8.20E+01 3.53E+03 1.06E+03 5.20E-04 -3.99E-01 -2.64E+00 4.74E-02 3.26E-01 1.35E-01 4.80E-01 3.08E+01 1.77E+01 7.61E-01 3.01E-01 6.39E+00 1.22E+02 1.71E+01 3.19E+03 6.75E+02 6.67E+03 3.94E+03 8.66E-01 6.42E-02 4.35E+00 1.34E-01 2.43E+00 3.58E+00 1.37E+02 3.03E+02 1.17E+04 4.57E-02 3.63E+06 3.63E+06 2.47E+02 2.13E+02 8.03E+00
TRU-Accumulation 3.93E-14 5.50E-04 3.41E-06 6.30E-05 6.28E-06 1.86E-09 2.64E+00 2.50E+00 8.33E-04 1.13E+00 3.05E-05 1.77E-02 7.07E-03 7.63E-08 1.47E-06 4.74E-12 2.31E-10 4.67E-06 1.94E-12 6.29E-08 5.45E-09 7.26E-03 2.34E-04 7.01E-05 2.54E-05 2.82E-02 5.37E-03 2.23E+00 2.70E-01 3.27E-01 7.48E-01 5.56E-05 1.33E-05 3.19E-05 5.76E-07 1.22E-05 3.85E-03 1.44E-04 5.41E-04 1.94E-02 3.44E-05 3.34E+01 3.34E+01 1.89E-02 1.73E-02 1.18E-02
LAW Accumulation 2.55E-05 3.33E-01 5.27E-02 6.10E-02 6.17E-03 3.92E-06 1.23E+00 1.16E+00 2.44E-02 5.31E-246 2.12E-249 2.16E-248 2.78E-248 7.55E-07 2.76E-03 7.01E-02 1.02E-252 2.04E-252 2.33E-252 1.01E-05 6.35E-04 2.72E-04 1.11E-05 1.08E-05 5.75E-04 2.54E-02 2.38E-04 6.20E-01 1.37E-01 4.96E-01 8.75E-01 1.42E-02 9.43E-06 3.35E-04 3.69E-03 8.24E-02 4.70E-02 6.09E-03 4.99E-249 5.42E-01 1.18E-02 1.57E+01 1.57E+01 4.85E-254 3.50E-248 5.52E+00
HLW-Accumulation 3.14E-08 6.95E-03 1.65E-04 3.32E-05 1.30E-03 1.62E-02 3.04E+03 2.87E+03 2.77E-05 9.26E+03 2.67E+00 1.03E+02 3.16E+01 9.36E-10 -2.78E-02 -5.72E-01 9.32E-04 7.39E-03 1.55E-03 5.63E-03 3.50E-01 1.26E-01 5.23E-03 3.49E-03 8.25E-02 2.44E+00 1.16E-01 6.11E+01 1.35E+01 1.55E+02 8.16E+01 7.37E-06 9.16E-04 8.14E-02 1.03E-06 2.29E-05 7.87E-01 1.98E+00 6.66E+00 1.76E+02 1.41E-05 7.00E+04 7.00E+04 8.94E+00 7.48E+00 2.22E-04
SLAW-Accumulation 1.40E-04 1.14E+00 1.33E+00 1.00E-01 5.77E-01 8.69E-05 2.11E+01 1.99E+01 3.05E-02 3.08E-20 1.22E-23 1.24E-22 1.58E-22 1.48E-05 9.20E-03 4.48E+00 5.92E-27 1.18E-26 1.35E-26 3.02E-05 1.93E-03 7.24E-04 2.97E-05 2.37E-05 1.42E-03 4.58E-02 6.52E-04 9.63E-01 2.14E-01 1.30E+00 1.39E+00 2.31E-02 1.43E-05 8.63E-04 5.51E-03 1.23E-01 1.66E-01 1.59E-02 2.56E-23 1.39E+00 2.67E-01 6.02E+02 6.02E+02 8.21E-25 4.47E-22 4.43E+02
LAWPS-Accumulation 3.55E-07 4.82E-04 2.67E-04 1.64E-04 9.12E-06 9.33E-05 2.19E+01 2.07E+01 5.35E-04 0.00E+00 0.00E+00 0.00E+00 0.00E+00 2.83E-09 7.10E-06 8.15E-05 0.00E+00 0.00E+00 0.00E+00 1.40E-08 9.57E-07 4.93E-07 2.09E-08 9.56E-09 4.42E-06 3.16E-06 4.69E-07 9.03E-05 1.73E-05 7.43E-04 1.01E-04 1.72E-05 1.09E-09 3.76E-07 2.55E-06 5.61E-05 5.11E-04 1.95E-07 0.00E+00 1.76E-05 5.13E-05 8.99E-02 8.99E-02 0.00E+00 0.00E+00 1.05E-02
ETF-Accumulation 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00
LERF-Accumulation 2.22E-06 1.76E-01 4.60E-02 1.16E-02 1.41E-04 8.99E-10 1.90E-04 1.79E-04 9.47E-03 1.48E-29 3.93E-34 2.05E-31 8.17E-32 3.99E-07 1.23E-03 1.08E-01 3.09E-39 6.30E-35 2.60E-41 2.06E-09 1.28E-07 4.82E-08 1.99E-09 1.48E-09 4.80E-08 1.70E-06 4.38E-08 4.12E-05 9.08E-06 8.20E-05 5.61E-05 2.66E-03 1.91E-06 5.34E-08 6.19E-04 1.38E-02 2.14E+00 1.67E-03 4.99E-29 1.48E-01 6.47E-03 1.25E+00 1.25E+00 2.21E-31 6.14E-27 4.09E-04
Total Accumulation 3.26E-04 7.01E+01 2.28E+01 2.51E+00 7.15E-01 1.60E+00 3.21E+05 3.03E+05 5.20E-01 4.22E+05 1.16E+02 4.83E+03 1.46E+03 5.41E-04 -7.62E-01 -5.04E+00 5.95E-02 4.28E-01 1.55E-01 5.55E-01 3.55E+01 1.95E+01 8.33E-01 3.55E-01 7.48E+00 1.54E+02 1.87E+01 3.97E+03 8.47E+02 8.67E+03 4.99E+03 9.95E-01 7.59E-02 5.40E+00 1.66E-01 3.15E+00 8.22E+00 1.64E+02 3.89E+02 1.41E+04 3.97E-01 4.60E+06 4.60E+06 3.66E+02 3.18E+02 4.82E+02
Accumulation minus TF and TRU 3.18E-04 4.01E+00 1.72E+00 5.51E-01 6.39E-01 1.58E+00 3.05E+05 2.88E+05 3.08E-01 1.19E+05 3.37E+01 1.30E+03 4.03E+02 2.02E-05 -3.63E-01 -2.40E+00 1.21E-02 1.02E-01 2.02E-02 7.49E-02 4.67E+00 1.75E+00 7.23E-02 5.40E-02 1.09E+00 3.13E+01 1.59E+00 7.78E+02 1.72E+02 1.99E+03 1.05E+03 1.29E-01 1.17E-02 1.05E+00 3.22E-02 7.19E-01 4.63E+00 2.71E+01 8.56E+01 2.40E+03 3.51E-01 9.69E+05 9.69E+05 1.19E+02 1.05E+02 4.74E+02
ADJUSTED INVENTORY TO INCLUDE ACCUMULATION-Radionuclides decayed to 1/1/2008 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
LAW Glass Subtotal (IDF) 1.19E+01 3.30E+03 4.04E+03 3.87E+02 1.65E+01 2.03E-01 1.05E+04 9.94E+03 0.00E+00 2.22E-01 8.85E-05 8.86E-04 1.12E-03 9.23E-03 1.30E+01 2.18E+02 4.17E-08 8.42E-08 9.43E-08 1.43E-01 9.94E+00 3.01E+00 1.22E-01 9.51E-02 1.73E+01 2.31E+02 2.70E+00 4.48E+03 9.45E+02 6.12E+03 7.42E+03 1.21E+02 7.37E-02 3.09E+00 1.33E+01 2.94E+02 0.00E+00 5.03E+01 1.82E-04 4.51E+03 1.41E+02 2.57E+05 2.57E+05 8.03E-04 5.73E-04 2.64E+04
LAW Spent Melter Subtotal (IDF) 1.27E-02 5.20E+00 4.36E+00 4.42E-01 2.38E-02 2.85E-04 1.36E+01 1.28E+01 0.00E+00 3.09E-04 1.23E-07 1.23E-06 1.56E-06 1.13E-05 1.88E-02 3.01E-01 5.80E-11 1.17E-10 1.31E-10 1.84E-04 1.29E-02 4.25E-03 1.73E-04 1.31E-04 2.09E-02 3.45E-01 3.85E-03 5.94E+00 1.25E+00 7.98E+00 9.82E+00 1.34E-01 1.01E-04 4.52E-03 1.57E-02 3.46E-01 0.00E+00 9.06E-02 2.53E-07 8.08E+00 1.80E-01 3.21E+02 3.21E+02 1.11E-06 7.98E-07 3.75E+01
ETF Solid Waste Form to IDF 6.59E-03 1.24E+01 6.87E+01 1.66E+00 6.42E-02 1.17E-05 6.70E-01 6.33E-01 3.52E+00 1.72E-05 4.62E-10 2.11E-07 8.42E-08 1.81E-04 5.82E-02 5.42E+00 3.73E-15 7.62E-11 3.12E-17 2.99E-07 1.78E-05 2.89E-03 1.21E-04 3.38E-05 7.08E-05 3.18E-04 2.78E-03 6.17E-03 1.28E-03 2.08E-02 9.72E-03 4.26E-01 3.41E-04 1.07E-05 4.90E-02 1.08E+00 2.34E+00 1.30E-01 8.75E-05 1.16E+01 2.86E+00 9.85E+01 9.85E+01 2.10E-07 5.85E-03 2.29E-01
Solid Waste Forms from Treatment Processes (IDF) 6.28E-05 7.98E-03 1.30E-02 1.92E-02 1.21E+01 8.28E-02 4.00E+03 3.77E+03 0.00E+00 2.74E-03 6.91E-07 4.15E-05 2.05E-05 3.51E-08 1.45E-06 8.29E-04 1.20E-09 4.05E-09 5.56E-09 2.29E-08 1.65E-06 5.16E-07 2.10E-08 1.58E-08 2.02E-06 1.12E-02 4.65E-07 2.02E-02 1.98E-02 1.05E-02 8.93E-04 3.94E-04 8.84E-09 7.71E-07 6.76E-04 1.10E-03 0.00E+00 4.24E-04 1.72E-05 3.79E-02 5.41E-03 2.63E+01 2.63E+01 2.77E-04 -1.06E-03 1.99E+01
Non-IDF Stream -2.14E-03 5.05E+02 1.51E+00 1.58E-01 6.11E-01 7.13E+02 3.90E+07 3.68E+07 8.24E+02 3.26E+06 8.23E+02 4.95E+04 2.45E+04 1.19E-05 -8.58E+00 -2.15E+02 1.43E+00 4.83E+00 6.63E+00 8.25E+00 6.41E+02 2.16E+02 8.83E+00 6.10E+00 9.11E+01 2.28E+03 1.96E+02 4.37E+04 9.25E+03 1.44E+05 7.25E+04 8.23E-02 6.89E-01 6.48E+01 5.05E-03 1.07E-01 2.81E+03 1.43E+03 3.80E+03 1.28E+05 4.52E-02 4.37E+07 4.37E+07 3.48E+03 2.95E+03 2.18E+01
TOTAL 1.20E+01 3.83E+03 4.11E+03 3.90E+02 2.93E+01 7.13E+02 3.90E+07 3.68E+07 8.27E+02 3.26E+06 8.23E+02 4.95E+04 2.45E+04 9.43E-03 4.51E+00 8.79E+00 1.43E+00 4.83E+00 6.63E+00 8.39E+00 6.51E+02 2.19E+02 8.95E+00 6.20E+00 1.08E+02 2.51E+03 1.99E+02 4.82E+04 1.02E+04 1.50E+05 7.99E+04 1.21E+02 7.63E-01 6.79E+01 1.34E+01 2.96E+02 2.81E+03 1.48E+03 3.80E+03 1.33E+05 1.44E+02 4.39E+07 4.39E+07 3.48E+03 2.95E+03 2.65E+04
100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 101% 107% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100%
ADJUSTED INVENTORY TO INCLUDE ACCUMULATION-Radionuclides decayed to 1/1/2051 IDF Waste Streams Only 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
LAW Glass Subtotal (IDF) 2.44E-12 3.99E+02 8.17E-02 3.87E+02 1.65E+01 1.10E-07 3.91E+03 3.69E+03 0.00E+00 1.60E-01 9.79E-06 2.76E-05 2.11E-06 9.06E-03 3.31E+00 1.23E+00 4.15E-08 8.42E-08 9.43E-08 9.32E-02 9.94E+00 3.01E+00 1.22E-01 9.51E-02 1.73E+01 1.65E+02 2.70E+00 4.47E+03 9.41E+02 5.92E+03 9.36E+02 9.76E+01 7.37E-02 3.08E+00 4.78E+00 5.67E+01 0.00E+00 5.03E+01 6.38E-07 3.35E+03 1.41E+02 9.13E+04 9.13E+04 8.03E-04 7.67E-04 2.64E+04
LAW Spent Melter Subtotal (IDF) 2.60E-15 6.28E-01 8.83E-05 4.42E-01 2.38E-02 1.53E-10 5.05E+00 4.77E+00 0.00E+00 2.22E-04 1.36E-08 3.84E-08 2.94E-09 1.11E-05 4.77E-03 1.70E-03 5.77E-11 1.17E-10 1.31E-10 1.20E-04 1.29E-02 4.25E-03 1.73E-04 1.31E-04 2.09E-02 2.45E-01 3.85E-03 5.93E+00 1.24E+00 7.72E+00 1.24E+00 1.08E-01 1.01E-04 4.50E-03 5.64E-03 6.67E-02 0.00E+00 9.05E-02 8.87E-10 6.02E+00 1.80E-01 1.14E+02 1.14E+02 1.11E-06 1.06E-06 3.74E+01
ETF Solid Waste Form to IDF 1.34E-15 1.50E+00 1.39E-03 1.66E+00 6.42E-02 6.31E-12 2.49E-01 2.35E-01 3.50E+00 1.24E-05 5.11E-11 6.57E-09 1.59E-10 1.77E-04 1.48E-02 3.07E-02 3.71E-15 7.62E-11 3.12E-17 1.95E-07 1.78E-05 2.89E-03 1.21E-04 3.38E-05 7.08E-05 2.27E-04 2.78E-03 6.17E-03 1.27E-03 1.96E-02 1.23E-03 3.45E-01 3.41E-04 1.06E-05 1.76E-02 2.08E-01 2.09E-01 1.30E-01 3.06E-07 8.65E+00 2.86E+00 3.50E+01 3.50E+01 2.10E-07 9.19E-04 2.29E-01
Solid Waste Forms from Treatment Processes (IDF) 1.28E-17 9.64E-04 2.64E-07 1.92E-02 1.21E+01 4.46E-08 1.48E+03 1.40E+03 0.00E+00 1.97E-03 7.65E-08 1.29E-06 3.87E-08 3.44E-08 3.72E-07 4.70E-06 1.19E-09 4.05E-09 5.56E-09 1.50E-08 1.65E-06 5.16E-07 2.10E-08 1.58E-08 2.02E-06 7.95E-03 4.65E-07 2.01E-02 1.97E-02 9.87E-03 1.13E-04 3.19E-04 8.84E-09 7.68E-07 2.43E-04 2.12E-04 0.00E+00 4.23E-04 6.02E-08 2.82E-02 5.41E-03 9.33E+00 9.33E+00 2.77E-04 6.69E-05 1.99E+01
SSW FRACTIONS BASED ON 10-010 and 10-009 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
HEPA fraction NR NR NR 51.81% 1.03% 52.45% 50.81% NR 10.40% NR 65.24% 64.99% 65.27% NR NR NR NR NR NR NR 68.98% 68.94% 68.90% 68.85% 54.86% 68.68% 68.39% 68.53% 68.48% 70.74% 68.04% NR NR NR NR NR 0.01% 56.98% 62.75% 57.75% 71.82% 65.75% NR NR NR 87.60%
IX Resin fraction NR NR NR 43.80% 0.14% 8.96% 9.27% NR 1.53% NR 7.64% 7.67% 7.61% NR NR NR NR NR NR NR 0.00% 0.00% 0.00% 0.00% 42.37% 0.00% 0.00% 0.00% 0.00% 3.83% 0.00% NR NR NR NR NR 49.09% 20.28% 19.08% 19.89% 26.01% 0.09% NR NR NR 11.86%
LAW and HLW Carbon Bed fraction NR NR NR 0.00% 36.47% 0.00% 0.00% NR 34.07% NR 0.00% 0.00% 0.00% NR NR NR NR NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR NR NR 36.25% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00%
Other Debris fraction NR NR NR 4.39% 0.01% 38.59% 39.92% NR 24.63% NR 27.13% 27.34% 27.12% NR NR NR NR NR NR NR 31.02% 31.06% 31.10% 31.15% 2.77% 31.32% 31.61% 31.47% 31.52% 25.43% 31.96% NR NR NR NR NR 14.62% 22.75% 18.17% 22.35% 2.17% 34.16% NR NR NR 0.54%
HLW Silver Mordenite Absorbent fraction NR NR NR 0.00% 62.35% 0.00% 0.00% NR 29.36% NR 0.00% 0.00% 0.00% NR NR NR NR NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR NR NR 0.03% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00%
WTP SSW INVENTORY-Radionuclides decayed to 1/1/2008 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
HEPA Filters Debris NR NR NR 9.93E-03 1.25E-01 4.34E-02 2.03E+03 NR 0.00E+00 NR 4.51E-07 2.70E-05 1.34E-05 NR NR NR NR NR NR NR 1.14E-06 3.56E-07 1.44E-08 1.09E-08 1.11E-06 7.67E-03 3.18E-07 1.38E-02 1.35E-02 7.46E-03 6.07E-04 NR NR NR NR NR 0.00E+00 2.41E-04 1.08E-05 2.19E-02 3.88E-03 1.73E+01 NR NR NR 1.74E+01
IX Resin Non-Debris NR NR NR 8.39E-03 1.66E-02 7.42E-03 3.71E+02 NR 0.00E+00 NR 5.28E-08 3.18E-06 1.56E-06 NR NR NR NR NR NR NR 5.54E-13 1.78E-13 6.14E-15 7.40E-15 8.54E-07 8.08E-08 1.63E-13 1.47E-07 1.45E-07 4.03E-04 6.61E-09 NR NR NR NR NR 0.00E+00 8.59E-05 3.28E-06 7.54E-03 1.41E-03 2.46E-02 NR NR NR 2.36E+00
LAW and HLW Carbon Beds Non-Debris NR NR NR 1.99E-13 4.42E+00 1.54E-11 6.30E-07 NR 0.00E+00 NR 1.43E-18 8.93E-17 4.37E-17 NR NR NR NR NR NR NR 6.18E-19 2.13E-19 8.95E-21 8.39E-21 2.03E-17 4.30E-15 1.95E-19 7.82E-15 7.65E-15 1.40E-14 3.50E-16 NR NR NR NR NR 0.00E+00 1.76E-14 1.11E-16 1.57E-12 3.94E-13 3.05E-09 NR NR NR 2.63E-09
Other Debris Debris NR NR NR 8.41E-04 1.09E-03 3.20E-02 1.60E+03 NR 0.00E+00 NR 1.87E-07 1.13E-05 5.57E-06 NR NR NR NR NR NR NR 5.13E-07 1.60E-07 6.52E-09 4.91E-09 5.58E-08 3.50E-03 1.47E-07 6.34E-03 6.24E-03 2.68E-03 2.85E-04 NR NR NR NR NR 0.00E+00 9.63E-05 3.12E-06 8.48E-03 1.17E-04 8.98E+00 NR NR NR 1.07E-01
HLW Silver Mordenite Absorbent Non-Debris NR NR NR 1.92E-16 7.56E+00 3.07E-11 1.25E-06 NR 0.00E+00 NR 3.59E-19 2.75E-17 1.32E-17 NR NR NR NR NR NR NR 1.24E-18 4.27E-19 1.79E-20 1.68E-20 1.32E-20 8.59E-15 3.90E-19 1.56E-14 1.53E-14 8.27E-15 7.00E-16 NR NR NR NR NR 0.00E+00 2.84E-14 2.38E-17 2.54E-12 4.83E-14 6.10E-09 NR NR NR 2.21E-12
SSW Total NR NR NR 1.92E-02 1.21E+01 8.28E-02 4.00E+03 NR 0.00E+00 NR 6.91E-07 4.15E-05 2.05E-05 NR NR NR NR NR NR NR 1.65E-06 5.16E-07 2.10E-08 1.58E-08 2.02E-06 1.12E-02 4.65E-07 2.02E-02 1.98E-02 1.05E-02 8.93E-04 NR NR NR NR NR 0.00E+00 4.24E-04 1.72E-05 3.79E-02 5.41E-03 2.63E+01 NR NR NR 1.99E+01
BBI 2.94E+01 3.90E+07 4.76E+07 2.65E+04
Check N/A N/A N/A 100% 100% 100% 100% N/A #DIV/0! N/A 100% 100% 100% N/A N/A N/A N/A N/A N/A N/A 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% N/A N/A N/A N/A N/A #DIV/0! 100% 100% 100% 100% 100% N/A N/A N/A 100%
WTP SSW INVENTORY-Radionuclides decayed to 1/1 2051 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
HEPA Filters Debris NR NR NR 9.93E-03 1.25E-01 2.34E-08 7.54E+02 NR 0.00E+00 NR 4.99E-08 8.40E-07 2.52E-08 NR NR NR NR NR NR NR 1.14E-06 3.56E-07 1.44E-08 1.09E-08 1.11E-06 5.46E-03 3.18E-07 1.38E-02 1.35E-02 6.98E-03 7.67E-05 NR NR NR NR NR 0.00E+00 2.41E-04 3.78E-08 1.63E-02 3.88E-03 6.14E+00 NR NR NR 1.74E+01
IX Resin Non-Debris NR NR NR 8.39E-03 1.66E-02 4.00E-09 1.38E+02 NR 0.00E+00 NR 5.84E-09 9.91E-08 2.94E-09 NR NR NR NR NR NR NR 5.54E-13 1.78E-13 6.14E-15 7.40E-15 8.54E-07 5.75E-08 1.63E-13 1.47E-07 1.44E-07 3.77E-04 8.34E-10 NR NR NR NR NR 0.00E+00 8.58E-05 1.15E-08 5.61E-03 1.41E-03 8.75E-03 NR NR NR 2.36E+00
LAW and HLW Carbon Beds Non-Debris NR NR NR 1.99E-13 4.42E+00 8.32E-18 2.34E-07 NR 0.00E+00 NR 1.58E-19 2.78E-18 8.23E-20 NR NR NR NR NR NR NR 6.18E-19 2.13E-19 8.95E-21 8.39E-21 2.03E-17 3.06E-15 1.95E-19 7.81E-15 7.61E-15 1.31E-14 4.42E-17 NR NR NR NR NR 0.00E+00 1.76E-14 3.90E-19 1.17E-12 3.93E-13 1.08E-09 NR NR NR 2.63E-09
Other Debris Debris NR NR NR 8.41E-04 1.09E-03 1.72E-08 5.92E+02 NR 0.00E+00 NR 2.07E-08 3.53E-07 1.05E-08 NR NR NR NR NR NR NR 5.13E-07 1.60E-07 6.52E-09 4.91E-09 5.58E-08 2.49E-03 1.47E-07 6.33E-03 6.21E-03 2.51E-03 3.60E-05 NR NR NR NR NR 0.00E+00 9.63E-05 1.09E-08 6.31E-03 1.17E-04 3.19E+00 NR NR NR 1.07E-01
HLW Silver Mordenite Absorbent Non-Debris NR NR NR 1.92E-16 7.56E+00 1.65E-17 4.64E-07 NR 0.00E+00 NR 3.97E-20 8.55E-19 2.48E-20 NR NR NR NR NR NR NR 1.24E-18 4.27E-19 1.79E-20 1.68E-20 1.32E-20 6.12E-15 3.90E-19 1.56E-14 1.52E-14 7.74E-15 8.83E-17 NR NR NR NR NR 0.00E+00 2.84E-14 8.32E-20 1.89E-12 4.83E-14 2.16E-09 NR NR NR 2.21E-12SE
CT
ION
5B
SE
CT
ION
1S
EC
TIO
N 2
SE
CT
ION
3A
SE
CT
ION
4S
EC
TIO
N 5
AS
EC
TIO
N 3
B
RPP-ENV-58562 Rev.03 5/9/2016 - 11:21 AM 100 of 118RPP-ENV-58562 Rev.03 9/26/2016 - 12:49 PM 100 of 124
RPP-ENV-58562, Rev. 3
A-5/A-6
Table A-2. Run Case 7 Chemicals.
SVF-4092, IDF PA Case 7 - Current Information Case - Mass Balance, MMR-50049.xlsm
WASTE STREAM Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
LAW Glass Subtotal (IDF) 1.11E+03 2.36E+07 4.67E+03 2.23E+07 9.73E+00 4.96E+02 6.46E+04 5.08E+03 5.30E+04 7.35E+05 4.87E+05 5.61E-01 3.56E+02 1.10E+06 2.83E+07 0.00E+00 9.37E+05 6.84E-05 7.75E+06 6.54E+06 6.99E-05 6.49E+03 8.02E+07 3.25E+03 2.25E+03 0.00E+00 0.00E+00 0.00E+00 7.00E+04 2.12E+03 0.00E+00 0.00E+00 7.52E+01 2.74E+02 0.00E+00 3.07E+03 3.48E+03 5.03E+03 1.61E+08 0.00E+00 3.12E+06 0.00E+00 6.05E+01 7.26E-02 1.53E+03 1.40E+03 8.54E-04 8.76E+06 2.34E-04 0.00E+00 8.03E+03 7.61E-01 4.14E+03 8.87E+01 1.73E+07 1.62E+07
LAW Spent Melter Subtotal (IDF) 1.70E+00 2.94E+04 6.22E+00 2.77E+04 1.39E-02 5.91E-01 8.75E+01 7.87E+00 8.77E+01 9.61E+02 7.39E+02 7.13E-04 4.70E-01 1.40E+03 3.52E+04 0.00E+00 1.27E+03 9.51E-08 7.47E+03 8.13E+03 9.72E-08 7.26E+00 1.07E+05 4.59E+00 3.29E+00 0.00E+00 0.00E+00 0.00E+00 7.59E+01 2.23E+00 0.00E+00 0.00E+00 9.96E-02 2.74E-01 0.00E+00 2.69E+00 4.39E+00 6.62E+00 1.97E+05 0.00E+00 3.63E+03 0.00E+00 7.72E-02 1.15E-04 2.17E+00 2.16E+00 1.19E-06 1.09E+04 3.37E-07 1.38E-02 1.14E+01 1.03E-03 2.89E+00 1.30E-01 2.16E+04 2.01E+04
ETF Solid Waste Form to IDF 3.13E+00 1.85E+01 9.61E+01 5.87E+01 7.39E-01 2.03E+00 3.16E+02 4.77E-01 1.14E+03 8.76E+02 4.27E+00 3.56E-05 3.52E+00 4.86E+03 3.13E+02 9.42E+02 6.87E+00 2.73E-03 7.97E+00 1.14E+00 3.38E+01 2.86E+01 3.55E+05 1.14E+01 6.40E+00 4.64E+01 1.64E+05 1.38E+05 8.82E+03 5.98E+00 2.39E+02 0.00E+00 1.88E-04 8.34E-01 0.00E+00 6.44E+00 7.18E+01 1.02E+02 1.88E+03 0.00E+00 0.00E+00 1.77E+03 1.18E+01 6.45E-04 1.33E-02 3.94E+01 2.83E-13 1.07E-05 1.45E-05 8.23E+03 8.25E+00 5.31E-05 2.67E-03 4.10E-03 2.25E+01 1.42E-05
Solid Waste Forms from Treatment Processes (IDF) 1.08E-01 2.17E+01 2.95E-01 2.88E+01 4.05E-02 5.56E-05 2.45E-02 3.29E-01 8.16E-04 8.00E+04 7.39E+02 2.10E-01 3.22E-03 1.04E+05 1.39E-01 9.85E+02 3.11E+02 8.73E-07 1.14E-01 8.70E-03 8.39E-02 1.41E-02 4.66E+03 3.13E-05 6.20E-01 0.00E+00 0.00E+00 0.00E+00 1.19E+01 2.38E-04 4.00E+03 6.70E-07 4.06E-04 1.05E-03 7.79E-07 8.14E-03 1.12E-02 4.95E-01 2.03E-01 5.84E+03 0.00E+00 0.00E+00 3.54E-02 2.19E-07 1.15E+00 2.33E-02 5.04E-05 2.84E-04 1.46E-04 0.00E+00 1.38E-03 2.83E-05 4.64E-04 2.70E-06 1.55E-01 3.23E-02
Non-IDF Stream 2.62E+03 2.52E+06 8.91E+01 1.44E+06 8.48E+03 2.76E+00 4.81E+05 3.58E+03 6.55E+03 4.95E+03 7.12E+04 2.07E+03 2.34E+03 3.29E+04 1.57E+06 1.38E+01 1.60E+04 4.21E+04 7.89E+05 2.24E+04 4.60E+05 2.34E+01 2.18E+06 5.95E+03 1.16E+05 1.69E+07 5.95E+07 2.63E+07 2.65E+03 6.08E-01 5.13E+06 7.99E+02 7.34E+02 9.95E-02 9.29E+02 7.42E-01 1.59E+02 3.39E+01 5.83E+06 -5.84E+03 -3.12E+06 3.78E+06 6.06E+04 2.51E+02 1.26E+00 1.47E+03 6.01E+04 1.38E+03 6.66E+03 8.60E+05 5.83E+05 2.37E+03 1.15E+01 4.75E+02 4.31E+02 4.06E+05
BBI 4.03E+03 8.67E+06 4.88E+03 1.52E+04 9.42E+03 5.02E+02 5.61E+05 8.87E+03 6.96E+03 8.27E+05 5.91E+05 2.09E+03 2.91E+03 1.28E+06 1.27E+06 1.99E+03 9.57E+05 3.20E+04 1.94E+03 2.19E+04 1.64E+05 6.56E+03 4.92E+07 9.70E+03 9.87E+04 1.19E+07 5.60E+07 4.45E+06 8.20E+04 2.14E+03 5.18E+06 8.43E+02 8.45E+02 2.78E+02 9.47E+02 3.09E+03 3.73E+03 5.18E+03 8.41E+05 0.00E+00 0.00E+00 3.82E+06 4.23E+04 2.72E+02 1.56E+03 2.92E+03 6.15E+04 1.51E+03 6.98E+03 8.71E+05 6.45E+05 2.58E+03 4.16E+03 5.81E+02 6.08E+03 4.09E+05
HTWOS Feed 4.03E+03 2.67E+07 4.88E+03 2.37E+07 9.42E+03 5.02E+02 6.02E+05 8.87E+03 6.14E+04 8.28E+05 5.91E+05 2.09E+03 2.91E+03 1.28E+06 3.00E+07 1.99E+03 9.57E+05 4.47E+04 8.54E+06 6.57E+06 4.80E+05 6.56E+03 8.30E+07 9.70E+03 1.25E+05 1.69E+07 5.97E+07 2.65E+07 8.20E+04 2.14E+03 5.20E+06 8.43E+02 8.77E+02 2.78E+02 9.47E+02 3.09E+03 3.73E+03 5.18E+03 1.67E+08 0.00E+00 0.00E+00 3.83E+06 6.38E+04 2.72E+02 1.56E+03 2.92E+03 6.15E+04 8.77E+06 6.98E+03 8.71E+05 6.47E+05 2.58E+03 4.16E+03 5.81E+02 1.74E+07 1.66E+07
HTWOS Feed Adjusted Minus TF and TRU Accumulation 3.82E+03 2.62E+07 4.87E+03 2.37E+07 8.70E+03 5.02E+02 5.47E+05 8.67E+03 6.10E+04 8.28E+05 5.63E+05 2.09E+03 2.73E+03 1.28E+06 2.99E+07 1.97E+03 9.56E+05 4.22E+04 8.54E+06 6.57E+06 4.68E+05 6.55E+03 8.29E+07 9.26E+03 1.20E+05 1.69E+07 5.97E+07 2.64E+07 8.16E+04 2.13E+03 5.14E+06 8.22E+02 8.23E+02 2.75E+02 9.40E+02 3.08E+03 3.72E+03 5.18E+03 1.67E+08 0.00E+00 0.00E+00 3.82E+06 6.09E+04 2.66E+02 1.56E+03 2.91E+03 6.03E+04 8.77E+06 6.79E+03 8.70E+05 5.96E+05 2.40E+03 4.15E+03 5.70E+02 1.74E+07 1.66E+07
ACCUMULATION STREAM Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
PT-Accumulation 9.18E+01 2.26E+04 2.01E+00 4.22E+00 1.85E+02 1.20E-01 3.07E+02 1.65E+00 1.63E+02 4.88E+02 2.20E+03 1.66E+01 2.50E+01 1.65E+03 1.16E+04 1.72E+00 9.27E+02 1.12E+02 6.63E-01 6.24E+02 7.13E+03 2.58E+00 4.96E+04 3.60E+01 1.13E+03 6.11E+03 5.96E+04 8.54E+03 3.67E+01 2.97E+00 2.61E+03 2.17E+01 1.22E+01 6.58E-03 1.02E+01 2.18E-02 1.70E+00 1.68E+00 9.42E+03 0.00E+00 0.00E+00 2.76E+03 2.24E+02 1.33E+01 1.49E+00 1.43E-01 1.69E+02 1.61E+01 1.27E+02 1.26E+03 4.42E+03 3.47E+01 2.46E-02 5.65E+00 2.87E+00 6.01E+02
TF-Accumulation 2.06E+02 4.65E+05 4.23E+00 2.53E+01 7.22E+02 3.31E-01 5.48E+04 1.98E+02 4.13E+02 5.98E+02 2.76E+04 9.09E-01 1.85E+02 6.23E+03 1.11E+05 1.73E+01 4.55E+02 2.50E+03 2.69E+00 1.68E+03 1.21E+04 3.51E+00 9.17E+04 4.49E+02 5.74E+03 6.43E+03 4.20E+04 6.24E+03 4.18E+02 7.34E+00 6.59E+04 2.08E+01 5.44E+01 3.50E+00 7.44E+00 5.07E+00 2.75E+00 2.71E+00 6.90E+04 0.00E+00 0.00E+00 2.66E+03 2.94E+03 5.93E+00 4.74E-01 3.00E+00 1.23E+03 1.15E+02 1.85E+02 7.70E+02 5.13E+04 1.79E+02 2.71E+00 1.08E+01 1.93E+01 1.80E+03
TRU-Accumulation 1.94E-02 2.91E+02 1.35E-02 2.92E-01 1.55E-01 6.08E-03 3.38E+02 9.73E-02 3.47E+00 1.25E+01 1.62E+01 1.47E-04 9.11E-01 1.57E+02 1.61E+02 2.34E-03 1.66E+00 1.96E-02 7.92E-115 2.52E+00 1.11E+00 3.96E-114 1.31E+03 7.92E-114 2.02E-01 3.37E+02 1.08E+03 1.08E-01 9.32E-01 0.00E+00 1.34E+03 0.00E+00 3.72E-02 0.00E+00 0.00E+00 1.13E-20 7.22E-01 8.75E-03 1.17E+02 0.00E+00 0.00E+00 7.15E+01 1.80E+00 0.00E+00 6.93E-04 0.00E+00 1.77E-08 1.73E-01 8.36E-113 5.54E+00 1.61E+01 2.50E-62 3.60E-299 6.08E-08 2.55E+00 1.21E+00
LAW Accumulation 1.37E-01 1.24E+03 3.51E-01 8.64E+02 5.32E-04 1.89E-02 7.17E+00 2.41E-01 3.43E+00 9.65E+01 9.87E+01 5.80E-05 1.69E-01 3.49E+02 1.10E+03 2.75E-01 1.48E+02 1.67E-249 1.08E-01 2.54E+02 1.71E-249 4.15E-01 8.07E+03 3.82E-01 2.41E-01 6.14E+02 2.67E+03 1.64E+03 3.86E+00 4.91E-01 2.75E+02 0.00E+00 1.06E-02 1.09E-03 0.00E+00 3.59E-03 3.00E-01 2.88E-01 5.84E+03 5.36E-02 8.73E+01 4.24E+02 4.45E-03 8.59E-06 3.26E-01 2.67E-02 2.12E-248 3.40E+02 1.61E-196 1.23E+02 7.14E-01 8.11E-05 4.04E-03 1.19E-02 6.72E+02 6.27E+02
HLW-Accumulation 2.97E+00 1.53E+03 5.69E-04 1.30E+03 1.57E+01 2.74E-05 2.64E+01 6.92E-03 7.31E+00 6.97E-03 8.58E+01 1.67E-01 1.80E+00 9.62E-02 9.95E+02 1.72E-03 1.11E+00 9.65E+00 3.09E+02 5.23E+01 6.12E+02 4.00E-04 1.38E+03 2.06E+00 9.46E+01 3.79E+00 1.24E+02 2.17E+01 9.41E-02 2.32E-04 2.00E-01 1.81E+00 1.04E+00 9.19E-06 8.63E-01 2.20E-05 4.14E-04 4.28E-04 3.63E+03 0.00E+00 3.51E-02 1.06E-01 1.65E+01 1.11E+00 1.31E-05 2.07E-04 1.41E+01 1.27E+00 7.56E+00 1.38E-01 3.48E+02 2.80E+00 2.55E-05 4.51E-01 3.79E-04 5.03E+01
SLAW-Accumulation 7.18E-01 1.51E+03 8.86E+00 8.61E+02 7.32E-03 3.97E-02 2.98E+01 1.12E+00 1.68E+01 5.38E+03 8.42E+02 7.08E-04 5.85E-01 3.17E+04 1.10E+03 3.09E+01 4.34E+02 9.80E-24 2.30E-01 2.53E+02 1.00E-23 1.01E+00 6.06E+04 9.55E-01 7.08E-01 7.71E+02 1.12E+04 3.01E+03 6.13E+00 8.83E-01 1.69E+03 0.00E+00 1.65E-02 8.48E-03 0.00E+00 1.86E-02 6.61E+00 8.08E+00 5.82E+03 2.65E-01 9.20E+01 4.04E+04 9.45E-02 5.42E-05 2.61E+01 1.51E+00 1.22E-22 3.38E+02 8.87E-15 1.52E+02 1.96E+00 4.31E-04 1.58E-02 2.98E-02 6.70E+02 6.25E+02
LAWPS-Accumulation 1.17E-05 3.77E-01 2.37E-03 6.54E-03 4.18E-06 2.39E-04 2.78E-02 4.58E-04 0.00E+00 4.07E-01 1.25E-01 1.21E-03 1.47E-04 6.89E-01 1.18E-02 1.07E-03 2.99E-01 0.00E+00 8.46E-04 0.00E+00 0.00E+00 2.89E-03 2.77E+01 3.60E-04 9.49E-06 8.53E+00 3.00E+01 2.82E+00 3.13E-02 2.13E-04 3.00E+00 0.00E+00 1.53E-06 7.53E-06 0.00E+00 2.69E-04 1.80E-03 2.57E-03 7.03E-02 0.00E+00 0.00E+00 2.41E+00 1.34E-05 3.75E-08 6.22E-04 8.54E-04 0.00E+00 0.00E+00 0.00E+00 3.35E-01 1.41E-03 3.75E-07 1.00E-04 1.05E-05 3.26E-03 0.00E+00
ETF-Accumulation 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00
LERF-Accumulation 4.26E-02 6.45E-03 2.04E-01 1.53E-01 3.88E-02 4.97E-03 3.04E+00 3.93E-03 8.55E+00 1.22E+00 4.56E-02 1.04E-08 3.99E-02 3.29E+01 3.12E+00 1.22E+00 2.31E-02 1.78E-28 2.70E-02 3.23E-25 2.73E-24 9.82E-02 1.76E+03 1.27E-01 7.55E-02 2.50E-03 3.49E+02 1.82E+03 2.04E+01 9.20E-02 1.28E-01 0.00E+00 1.18E-06 9.44E-04 0.00E+00 2.46E-03 1.59E-01 1.80E-01 1.27E+01 0.00E+00 0.00E+00 7.78E+00 6.11E-02 1.36E-05 2.41E-05 4.89E-02 2.36E-37 2.51E-30 5.27E-32 8.57E+01 1.31E-04 5.12E-05 2.57E-03 3.94E-03 9.33E-02 1.45E-29
Total Accumulation 3.02E+02 4.92E+05 1.57E+01 3.06E+03 9.23E+02 5.22E-01 5.55E+04 2.01E+02 6.16E+02 6.58E+03 3.09E+04 1.76E+01 2.14E+02 4.01E+04 1.26E+05 5.14E+01 1.97E+03 2.62E+03 3.13E+02 2.87E+03 1.99E+04 7.61E+00 2.14E+05 4.89E+02 6.97E+03 1.43E+04 1.17E+05 2.13E+04 4.86E+02 1.18E+01 7.18E+04 4.44E+01 6.77E+01 3.51E+00 1.85E+01 5.12E+00 1.22E+01 1.30E+01 9.38E+04 3.19E-01 1.79E+02 4.63E+04 3.18E+03 2.03E+01 2.84E+01 4.72E+00 1.41E+03 8.10E+02 3.19E+02 2.39E+03 5.61E+04 2.16E+02 2.75E+00 1.69E+01 1.37E+03 3.70E+03
Accumulation minus TF and TRU 9.57E+01 2.69E+04 1.14E+01 3.03E+03 2.01E+02 1.84E-01 3.73E+02 3.02E+00 1.99E+02 5.97E+03 3.23E+03 1.67E+01 2.76E+01 3.37E+04 1.48E+04 3.41E+01 1.51E+03 1.22E+02 3.10E+02 1.18E+03 7.74E+03 4.10E+00 1.21E+05 3.95E+01 1.23E+03 7.50E+03 7.40E+04 1.50E+04 6.73E+01 4.44E+00 4.58E+03 2.35E+01 1.33E+01 1.71E-02 1.11E+01 4.68E-02 8.77E+00 1.02E+01 2.47E+04 3.19E-01 1.79E+02 4.36E+04 2.41E+02 1.44E+01 2.79E+01 1.73E+00 1.83E+02 6.95E+02 1.34E+02 1.62E+03 4.77E+03 3.75E+01 4.72E-02 6.14E+00 1.35E+03 1.90E+03
ADJUSTED INVENTORY TO INCLUDE ACCUMULATION Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
LAW Glass Subtotal (IDF) 1.13E+03 2.36E+07 4.68E+03 2.23E+07 9.95E+00 4.96E+02 6.46E+04 5.09E+03 5.32E+04 7.40E+05 4.90E+05 5.65E-01 3.60E+02 1.13E+06 2.83E+07 0.00E+00 9.39E+05 6.86E-05 7.75E+06 6.54E+06 7.10E-05 6.50E+03 8.03E+07 3.27E+03 2.27E+03 0.00E+00 0.00E+00 0.00E+00 7.01E+04 2.12E+03 0.00E+00 0.00E+00 7.64E+01 2.74E+02 0.00E+00 3.07E+03 3.49E+03 5.04E+03 1.61E+08 #DIV/0! #DIV/0! 0.00E+00 6.08E+01 7.66E-02 1.56E+03 1.40E+03 8.57E-04 8.76E+06 2.39E-04 0.00E+00 8.10E+03 7.72E-01 4.14E+03 8.97E+01 1.73E+07 1.62E+07
LAW Spent Melter Subtotal (IDF) 1.74E+00 2.95E+04 6.23E+00 2.77E+04 1.42E-02 5.91E-01 8.76E+01 7.87E+00 8.80E+01 9.68E+02 7.44E+02 7.19E-04 4.75E-01 1.44E+03 3.52E+04 0.00E+00 1.27E+03 9.54E-08 7.47E+03 8.14E+03 9.88E-08 7.27E+00 1.07E+05 4.61E+00 3.32E+00 0.00E+00 0.00E+00 0.00E+00 7.59E+01 2.24E+00 0.00E+00 0.00E+00 1.01E-01 2.74E-01 0.00E+00 2.69E+00 4.40E+00 6.64E+00 1.97E+05 #DIV/0! #DIV/0! 0.00E+00 7.75E-02 1.21E-04 2.21E+00 2.16E+00 1.19E-06 1.09E+04 3.44E-07 1.38E-02 1.15E+01 1.04E-03 2.89E+00 1.31E-01 2.16E+04 2.01E+04
ETF Solid Waste Form to IDF 3.21E+00 1.85E+01 9.63E+01 5.87E+01 7.56E-01 2.03E+00 3.17E+02 4.77E-01 1.14E+03 8.83E+02 4.30E+00 3.59E-05 3.56E+00 4.99E+03 3.13E+02 9.58E+02 6.88E+00 2.74E-03 7.97E+00 1.14E+00 3.44E+01 2.86E+01 3.56E+05 1.15E+01 6.47E+00 4.64E+01 1.64E+05 1.38E+05 8.82E+03 5.99E+00 2.40E+02 0.00E+00 1.91E-04 8.34E-01 0.00E+00 6.44E+00 7.20E+01 1.02E+02 1.88E+03 #DIV/0! #DIV/0! 1.79E+03 1.18E+01 6.80E-04 1.35E-02 3.94E+01 2.84E-13 1.07E-05 1.48E-05 8.24E+03 8.32E+00 5.39E-05 2.67E-03 4.15E-03 2.25E+01 1.42E-05
Solid Waste Forms from Treatment Processes (IDF) 1.10E-01 2.17E+01 2.95E-01 2.88E+01 4.14E-02 5.56E-05 2.45E-02 3.30E-01 8.19E-04 8.06E+04 7.43E+02 2.12E-01 3.26E-03 1.06E+05 1.39E-01 1.00E+03 3.12E+02 8.76E-07 1.14E-01 8.70E-03 8.53E-02 1.41E-02 4.66E+03 3.14E-05 6.27E-01 0.00E+00 0.00E+00 0.00E+00 1.19E+01 2.38E-04 4.00E+03 6.89E-07 4.12E-04 1.05E-03 7.88E-07 8.14E-03 1.13E-02 4.96E-01 2.03E-01 #DIV/0! #DIV/0! 0.00E+00 3.56E-02 2.31E-07 1.17E+00 2.33E-02 5.05E-05 2.84E-04 1.48E-04 0.00E+00 1.39E-03 2.87E-05 4.64E-04 2.73E-06 1.55E-01 3.23E-02
Non-IDF Stream 2.68E+03 2.53E+06 8.93E+01 1.44E+06 8.68E+03 2.76E+00 4.82E+05 3.58E+03 6.57E+03 4.98E+03 7.16E+04 2.09E+03 2.36E+03 3.37E+04 1.57E+06 1.40E+01 1.60E+04 4.22E+04 7.89E+05 2.24E+04 4.67E+05 2.34E+01 2.19E+06 5.97E+03 1.17E+05 1.69E+07 5.95E+07 2.63E+07 2.66E+03 6.09E-01 5.13E+06 8.22E+02 7.46E+02 9.95E-02 9.40E+02 7.42E-01 1.59E+02 3.40E+01 5.84E+06 #DIV/0! #DIV/0! 3.82E+06 6.08E+04 2.65E+02 1.28E+00 1.47E+03 6.03E+04 1.38E+03 6.79E+03 8.62E+05 5.88E+05 2.40E+03 1.15E+01 4.80E+02 4.31E+02 4.06E+05
TOTAL 3.82E+03 2.62E+07 4.87E+03 2.37E+07 8.69E+03 5.02E+02 5.47E+05 8.67E+03 6.10E+04 8.28E+05 5.63E+05 2.09E+03 2.73E+03 1.28E+06 2.99E+07 1.97E+03 9.56E+05 4.22E+04 8.54E+06 6.57E+06 4.68E+05 6.55E+03 8.29E+07 9.25E+03 1.20E+05 1.69E+07 5.97E+07 2.64E+07 8.16E+04 2.13E+03 5.14E+06 8.22E+02 8.23E+02 2.75E+02 9.40E+02 3.08E+03 3.72E+03 5.18E+03 1.67E+08 #DIV/0! #DIV/0! 3.82E+06 6.09E+04 2.65E+02 1.56E+03 2.91E+03 6.03E+04 8.77E+06 6.79E+03 8.70E+05 5.96E+05 2.40E+03 4.15E+03 5.70E+02 1.74E+07 1.66E+07
100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% #DIV/0! #DIV/0! 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100%
SSW FRACTIONS BASED ON 10-010 and 10-009 Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
HEPA fraction 4.53% 17.39% 17.89% 62.10% 6.43% 0.15% 5.17% 50.79% 0.21% 0.00% 94.18% NR 0.00% 0.00% 44.22% 0.00% 56.46% 7.86% 91.84% 69.10% 12.79% NR 40.68% 4.20% 13.13% NR NR NR 61.05% 1.03% NR #DIV/0! 8.09% 5.61% 5.04% 78.35% 5.42% 31.35% 41.49% NR NR NR 15.98% 0.00% 63.36% 20.43% 7.69% 71.77% 23.04% NR 8.06% 41.24% 0.23% NR 87.47% 60.66%
IX Resin fraction 43.06% 62.12% 53.58% 0.54% 22.10% 93.91% 29.47% 23.43% 90.28% 95.63% 5.35% NR 0.00% 0.08% 0.00% 0.00% 42.37% 5.18% 0.04% 0.12% 0.00% NR 55.24% 45.56% 38.04% NR NR NR 19.53% 83.67% NR #DIV/0! 0.00% 61.81% 76.38% 0.00% 72.52% 63.57% 0.12% NR NR NR 0.23% 0.00% 34.99% 4.19% 25.51% 0.00% 38.40% NR 0.00% 16.62% 93.95% NR 0.01% 0.38%
LAW and HLW Carbon Bed fraction 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 98.32% 0.00% 100.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% NR #DIV/0! 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0.00% 0.00% NR 0.00% 0.00%
Other Debris fraction 52.41% 20.48% 28.53% 37.37% 71.47% 5.95% 65.36% 25.78% 9.52% 4.37% 0.47% NR 100.00% 0.01% 55.78% 0.00% 1.17% 86.96% 8.12% 30.78% 87.21% NR 4.08% 50.24% 48.83% NR NR NR 19.42% 15.31% NR #DIV/0! 91.91% 32.59% 18.58% 21.65% 22.06% 5.08% 58.40% NR NR NR 83.79% 100.00% 1.65% 75.39% 66.80% 28.23% 38.56% NR 91.94% 42.15% 5.83% NR 12.52% 38.96%
HLW Silver Mordenite Absorbent fraction 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 1.59% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% NR #DIV/0! 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0.00% 0.00% NR 0.00% 0.00%
WTP SSW INVENTORY Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
HEPA Filters Debris 5.00E-03 3.78E+00 5.28E-02 1.79E+01 2.66E-03 8.13E-08 1.27E-03 1.67E-01 1.70E-06 0.00E+00 7.00E+02 NR 0.00E+00 1.69E-01 6.13E-02 0.00E+00 1.76E+02 6.88E-08 1.05E-01 6.02E-03 1.09E-02 NR 1.90E+03 1.32E-06 8.23E-02 NR NR NR 7.27E+00 2.45E-06 NR #DIV/0! 3.33E-05 5.91E-05 3.97E-08 6.38E-03 6.11E-04 1.56E-01 8.41E-02 NR NR NR 5.68E-03 0.00E+00 7.44E-01 4.77E-03 3.89E-06 2.04E-04 3.42E-05 NR 1.12E-04 1.19E-05 1.05E-06 NR 1.36E-01 1.96E-02
IX Resin Non-Debris 4.75E-02 1.35E+01 1.58E-01 1.54E-01 9.15E-03 5.22E-05 7.22E-03 7.72E-02 7.39E-04 7.71E+04 3.98E+01 NR 0.00E+00 8.99E+01 5.52E-07 2.24E-02 1.32E+02 4.54E-08 4.16E-05 1.01E-05 1.88E-08 NR 2.58E+03 1.43E-05 2.38E-01 NR NR NR 2.33E+00 1.99E-04 NR #DIV/0! 8.60E-09 6.52E-04 6.02E-07 1.20E-08 8.17E-03 3.15E-01 2.41E-04 NR NR NR 8.16E-05 0.00E+00 4.11E-01 9.77E-04 1.29E-05 4.94E-12 5.70E-05 NR 1.39E-09 4.78E-06 4.36E-04 NR 1.21E-05 1.23E-04
LAW and HLW Carbon Beds Non-Debris 1.27E-12 2.54E-09 7.44E-11 1.33E-08 3.60E-13 1.24E-15 1.99E-13 2.50E-10 1.70E-14 4.23E-02 7.26E-10 NR 0.00E+00 1.05E+05 3.65E-11 1.00E+03 1.07E-07 1.52E-18 6.31E-11 3.61E-12 1.09E-11 NR 1.20E-06 3.39E-16 7.37E-11 NR NR NR 5.40E-09 4.76E-15 NR #DIV/0! 4.61E-16 3.36E-14 3.16E-17 1.82E-11 7.37E-13 1.64E-10 5.05E-11 NR NR NR 1.01E-11 0.00E+00 4.59E-10 7.81E-12 1.06E-15 1.23E-13 1.59E-14 NR 1.58E-15 7.05E-15 1.03E-14 NR 8.11E-11 1.18E-11
Other Debris Debris 5.78E-02 4.45E+00 8.43E-02 1.08E+01 2.96E-02 3.31E-06 1.60E-02 8.50E-02 7.79E-05 3.52E+03 3.47E+00 NR 3.26E-03 5.58E+00 7.74E-02 2.01E-03 3.65E+00 7.62E-07 9.28E-03 2.68E-03 7.44E-02 NR 1.90E+02 1.58E-05 3.06E-01 NR NR NR 2.31E+00 3.64E-05 NR #DIV/0! 3.79E-04 3.44E-04 1.46E-07 1.76E-03 2.49E-03 2.52E-02 1.18E-01 NR NR NR 2.98E-02 2.31E-07 1.94E-02 1.76E-02 3.38E-05 8.03E-05 5.73E-05 NR 1.28E-03 1.21E-05 2.70E-05 NR 1.94E-02 1.26E-02
HLW Silver Mordenite Absorbent Non-Debris 1.02E-13 8.36E-11 1.09E-10 1.53E-10 1.45E-13 1.66E-19 2.83E-14 3.82E-10 5.54E-17 2.18E-07 6.10E-10 NR 0.00E+00 1.69E+03 2.71E-13 7.92E-03 1.56E-09 9.51E-19 1.31E-13 2.34E-14 1.88E-11 NR 2.06E-09 1.88E-17 8.00E-11 NR NR NR 2.76E-09 6.27E-17 NR #DIV/0! 9.22E-16 1.42E-15 3.64E-19 3.64E-11 7.29E-13 1.62E-10 2.08E-13 NR NR NR 2.02E-11 0.00E+00 3.87E-13 1.54E-11 7.50E-17 8.71E-16 1.85E-15 NR 3.15E-15 5.30E-17 3.11E-19 NR 1.44E-15 4.28E-14
SSW Total 1.10E-01 2.17E+01 2.95E-01 2.88E+01 4.14E-02 5.56E-05 2.45E-02 3.30E-01 8.19E-04 8.06E+04 7.43E+02 NR 3.26E-03 1.06E+05 1.39E-01 1.00E+03 3.12E+02 8.76E-07 1.14E-01 8.70E-03 8.53E-02 NR 4.66E+03 3.14E-05 6.27E-01 NR NR NR 1.19E+01 2.38E-04 NR #DIV/0! 4.12E-04 1.05E-03 7.88E-07 8.14E-03 1.13E-02 4.96E-01 2.03E-01 NR NR NR 3.56E-02 2.31E-07 1.17E+00 2.33E-02 5.05E-05 2.84E-04 1.48E-04 NR 1.39E-03 2.87E-05 4.64E-04 NR 1.55E-01 3.23E-02
BBI 5.91E+05 1.99E+03 8.20E+04
Check 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% N/A 100% 100% 100% 100% 100% 100% 100% 100% 100% N/A 100% 100% 100% N/A N/A N/A 100% 100% N/A #DIV/0! 100% 100% 100% 100% 100% 100% 100% N/A N/A N/A 100% 100% 100% 100% 100% 100% 100% N/A 100% 100% 100% N/A 100% 100%
SE
CT
ION
1S
EC
TIO
N 2
SE
CT
ION
3A
SE
CT
ION
4S
EC
TIO
N 5
A
RPP-ENV-58562 Rev.03 5/9/2016 - 11:21 AM 101 of 118RPP-ENV-58562 Rev.03 9/26/2016 - 12:49 PM 101 of 124
RPP-ENV-58562, Rev. 3
A-7/A-8
Table A-3. Run Case 8B Radionuclides.
SVF-4094, IDF PA Case 8B - Tc_Tc-99 Removal from LAW Vitrification Off-Gas Condensate - Mass Balance, MMR-50051
WASTE STREAM 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
LAW Glass Subtotal (IDF) 1.20E+01 3.32E+03 4.03E+03 3.87E+02 1.62E+01 3.07E-01 1.39E+04 1.31E+04 0.00E+00 2.09E-01 8.29E-05 8.42E-04 1.08E-03 9.20E-03 1.33E+01 1.85E+02 4.03E-08 8.05E-08 9.17E-08 1.46E-01 1.02E+01 2.96E+00 1.20E-01 9.60E-02 1.71E+01 2.37E+02 2.65E+00 4.49E+03 9.59E+02 6.03E+03 7.59E+03 1.21E+02 7.51E-02 3.04E+00 1.33E+01 2.94E+02 0.00E+00 4.98E+01 1.74E-04 4.45E+03 1.40E+02 1.82E+05 1.82E+05 7.57E-04 5.40E-04 9.96E+03
LAW Spent Melter Subtotal (IDF) 1.14E-02 4.28E+00 3.77E+00 4.17E-01 1.61E-02 2.45E-04 1.19E+01 1.12E+01 0.00E+00 2.53E-04 1.00E-07 1.02E-06 1.30E-06 1.03E-05 1.60E-02 2.08E-01 4.87E-11 9.72E-11 1.11E-10 1.28E-04 9.23E-03 3.26E-03 1.32E-04 1.07E-04 1.91E-02 3.01E-01 2.92E-03 5.55E+00 1.18E+00 6.47E+00 9.22E+00 1.13E-01 9.68E-05 3.56E-03 1.31E-02 2.89E-01 0.00E+00 6.03E-02 2.10E-07 5.37E+00 1.58E-01 1.62E+02 1.62E+02 9.17E-07 6.49E-07 1.11E+01
ETF Solid Waste Form to IDF 6.35E-03 1.27E+01 6.93E+01 1.62E+00 6.44E-02 9.64E-06 6.01E-01 5.68E-01 3.67E+00 1.66E-05 4.44E-10 2.06E-07 8.28E-08 1.80E-04 6.19E-02 4.28E+00 3.69E-15 7.47E-11 3.11E-17 3.01E-07 1.78E-05 2.87E-03 1.20E-04 3.35E-05 7.12E-05 3.15E-04 2.75E-03 6.34E-03 1.31E-03 2.11E-02 9.87E-03 4.22E-01 3.45E-04 1.07E-05 4.79E-02 1.05E+00 3.25E+00 1.24E-01 8.56E-05 1.10E+01 2.85E+00 9.32E+01 9.32E+01 2.03E-07 5.65E-03 2.89E-02
Solid Waste Forms from Treatment Processes (IDF) 6.28E-05 7.89E-03 1.30E-02 1.80E-02 1.19E+01 8.19E-02 3.89E+03 3.67E+03 0.00E+00 2.70E-03 6.82E-07 4.11E-05 2.04E-05 3.50E-08 1.48E-06 7.04E-04 1.19E-09 4.01E-09 5.55E-09 2.33E-08 1.68E-06 5.09E-07 2.07E-08 1.58E-08 1.99E-06 1.03E-02 4.58E-07 1.87E-02 1.83E-02 9.88E-03 9.12E-04 3.70E-04 8.99E-09 7.60E-07 6.20E-04 9.94E-04 0.00E+00 4.19E-04 1.70E-05 3.75E-02 5.40E-03 2.62E+01 2.62E+01 2.71E-04 -9.45E-04 1.35E+01
Non-IDF Stream -1.09E-02 4.85E+02 1.38E+00 1.94E-01 6.00E-01 7.10E+02 3.87E+07 3.65E+07 8.23E+02 3.22E+06 8.13E+02 4.91E+04 2.43E+04 1.31E-05 -8.66E+00 -1.80E+02 1.42E+00 4.78E+00 6.62E+00 8.22E+00 6.40E+02 2.15E+02 8.77E+00 6.07E+00 9.06E+01 2.27E+03 1.95E+02 4.35E+04 9.20E+03 1.43E+05 7.20E+04 1.06E-01 6.84E-01 6.46E+01 7.50E-03 1.56E-01 2.80E+03 1.42E+03 3.76E+03 1.27E+05 5.58E-02 4.35E+07 4.35E+07 3.41E+03 2.88E+03 1.65E+04
BBI 1.20E+01 3.89E+03 4.13E+03 3.91E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 5.51E+02 3.57E+06 9.07E+02 5.30E+04 2.55E+04 9.95E-03 4.14E+00 6.77E+00 1.48E+00 5.16E+00 6.77E+00 8.87E+00 6.82E+02 2.37E+02 9.71E+00 6.50E+00 1.15E+02 2.63E+03 2.15E+02 4.94E+04 1.08E+04 1.57E+05 8.38E+04 1.22E+02 8.26E-01 7.23E+01 1.35E+01 2.98E+02 2.82E+03 1.62E+03 4.10E+03 1.44E+05 1.44E+02 4.76E+07 4.76E+07 3.73E+03 3.17E+03 2.65E+04
HTWOS Feed 1.20E+01 3.89E+03 4.13E+03 3.91E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 8.28E+02 3.57E+06 9.07E+02 5.30E+04 2.55E+04 9.95E-03 4.14E+00 6.77E+00 1.48E+00 5.16E+00 6.77E+00 8.87E+00 6.82E+02 2.37E+02 9.71E+00 6.50E+00 1.15E+02 2.64E+03 2.16E+02 5.14E+04 1.09E+04 1.57E+05 8.39E+04 1.22E+02 8.27E-01 7.23E+01 1.35E+01 2.98E+02 2.82E+03 1.62E+03 4.10E+03 1.44E+05 1.44E+02 4.76E+07 4.76E+07 3.73E+03 3.17E+03 2.65E+04
HTWOS Feed Adjusted Minus TF and TRU Accumulation 1.20E+01 3.83E+03 4.11E+03 3.90E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 8.27E+02 3.27E+06 8.25E+02 4.95E+04 2.45E+04 9.43E-03 4.52E+00 8.62E+00 1.43E+00 4.84E+00 6.64E+00 8.39E+00 6.51E+02 2.19E+02 8.95E+00 6.20E+00 1.08E+02 2.52E+03 1.99E+02 4.83E+04 1.02E+04 1.50E+05 8.00E+04 1.21E+02 7.64E-01 6.80E+01 1.34E+01 2.96E+02 2.81E+03 1.48E+03 3.80E+03 1.33E+05 1.44E+02 4.40E+07 4.40E+07 3.49E+03 2.96E+03 2.65E+04
ACCUMULATION STREAM 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
PT-Accumulation 1.78E-04 1.85E+00 2.85E-01 1.18E-01 5.80E-02 2.90E+00 2.84E+05 2.68E+05 3.34E-01 4.61E+04 1.13E+01 4.13E+02 1.71E+02 3.91E-06 -1.69E-01 -3.03E+00 9.84E-03 5.01E-02 1.26E-02 2.38E-02 1.31E+00 1.30E+00 5.51E-02 2.92E-02 5.98E-01 9.52E+00 1.25E+00 2.36E+02 5.07E+01 6.65E+02 3.24E+02 1.92E-02 3.57E-03 3.00E-01 9.04E-04 1.99E-02 2.16E+00 1.42E+01 3.57E+01 1.27E+03 6.65E-02 2.56E+05 2.56E+05 7.90E+01 7.36E+01 8.35E+00
TF-Accumulation 7.93E-06 6.50E+01 2.11E+01 1.96E+00 7.51E-02 2.37E-02 1.63E+04 1.54E+04 2.10E-01 3.01E+05 8.13E+01 3.50E+03 1.05E+03 5.20E-04 -3.80E-01 -1.85E+00 4.68E-02 3.24E-01 1.32E-01 4.77E-01 3.05E+01 1.77E+01 7.59E-01 2.99E-01 6.37E+00 1.21E+02 1.71E+01 3.15E+03 6.67E+02 6.61E+03 3.89E+03 8.66E-01 6.37E-02 4.31E+00 1.34E-01 2.43E+00 3.58E+00 1.36E+02 3.02E+02 1.16E+04 4.56E-02 3.61E+06 3.61E+06 2.44E+02 2.11E+02 8.02E+00
TRU-Accumulation 3.93E-14 5.50E-04 3.41E-06 6.30E-05 6.28E-06 1.86E-09 2.64E+00 2.50E+00 8.33E-04 1.13E+00 3.05E-05 1.77E-02 7.07E-03 7.63E-08 1.47E-06 4.74E-12 2.31E-10 4.67E-06 1.94E-12 6.29E-08 5.45E-09 7.26E-03 2.34E-04 7.01E-05 2.54E-05 2.82E-02 5.37E-03 2.23E+00 2.70E-01 3.27E-01 7.48E-01 5.56E-05 1.33E-05 3.19E-05 5.76E-07 1.22E-05 3.85E-03 1.44E-04 5.41E-04 1.94E-02 3.44E-05 3.34E+01 3.34E+01 1.89E-02 1.73E-02 1.18E-02
LAW Accumulation 3.60E-05 3.76E-01 6.21E-02 1.93E-02 5.19E-03 3.57E-06 6.65E-01 6.27E-01 3.49E-02 5.41E-247 2.17E-250 2.23E-249 2.90E-249 7.71E-07 1.18E-03 9.09E-02 1.04E-253 2.08E-253 2.37E-253 2.88E-06 1.70E-04 2.29E-04 9.74E-06 4.93E-06 9.55E-04 2.42E-02 2.18E-04 6.50E-01 1.36E-01 8.15E-02 9.16E-01 3.15E-03 9.63E-06 5.58E-05 1.50E-04 3.31E-03 1.09E-01 1.96E-02 5.06E-250 1.77E+00 1.26E-02 1.49E+01 1.49E+01 3.12E-255 3.59E-249 2.08E+00
HLW-Accumulation 3.99E-08 2.18E-03 2.16E-04 2.85E-05 8.76E-04 5.66E-02 6.47E+03 6.11E+03 1.59E-05 3.37E+03 8.30E-01 3.02E+01 1.25E+01 1.82E-09 -1.27E-02 -2.61E-01 7.10E-04 3.64E-03 8.67E-04 1.69E-03 9.23E-02 8.80E-02 3.73E-03 2.00E-03 4.22E-02 6.40E-01 8.45E-02 1.58E+01 3.40E+00 4.79E+01 2.16E+01 3.24E-06 2.39E-04 2.15E-02 1.90E-07 4.17E-06 7.58E-01 9.94E-01 2.58E+00 8.85E+01 1.93E-05 1.80E+04 1.80E+04 5.82E+00 4.81E+00 3.03E-04
SLAW-Accumulation 1.85E-04 8.45E-01 1.63E+00 3.44E-02 4.70E-01 1.15E-04 1.33E+01 1.26E+01 3.63E-02 3.64E-22 1.44E-25 1.47E-24 1.88E-24 1.95E-05 2.80E-03 1.54E+00 7.01E-29 1.40E-28 1.59E-28 8.11E-06 4.59E-04 4.54E-04 1.93E-05 1.03E-05 1.64E-03 4.32E-02 4.35E-04 1.11E+00 2.37E-01 2.51E-01 1.54E+00 4.77E-03 1.59E-05 1.38E-04 2.50E-04 5.49E-03 3.13E-01 2.95E-02 3.03E-25 2.64E+00 2.66E-01 3.95E+01 3.95E+01 8.21E-27 5.03E-24 2.60E+00
LAWPS-Accumulation 4.58E-07 1.78E-04 3.82E-04 1.23E-04 8.18E-06 7.53E-05 1.85E+01 1.74E+01 4.76E-04 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.08E-09 8.23E-06 1.72E-04 0.00E+00 0.00E+00 0.00E+00 1.34E-08 9.05E-07 5.73E-07 2.41E-08 1.78E-08 4.03E-06 1.95E-06 5.31E-07 5.59E-05 9.85E-06 1.21E-03 7.05E-05 3.71E-05 6.53E-10 6.31E-07 5.60E-06 1.24E-04 5.08E-04 5.60E-08 0.00E+00 5.03E-06 4.06E-05 9.66E-02 9.66E-02 0.00E+00 0.00E+00 8.36E-03
ETF-Accumulation 5.39E-05 4.40E-03 2.07E-01 3.34E-04 5.14E-03 8.02E-06 2.70E-01 2.55E-01 0.00E+00 8.63E-07 3.42E-10 3.47E-09 4.44E-09 4.76E-07 9.67E-06 1.61E-04 1.66E-13 3.32E-13 3.78E-13 1.10E-07 5.83E-06 1.24E-06 4.79E-08 6.60E-08 1.64E-05 2.26E-05 9.86E-07 3.39E-04 8.27E-05 3.66E-04 7.59E-04 8.49E-05 7.58E-08 5.55E-08 9.49E-06 2.10E-04 2.09E-01 3.95E-05 8.20E-10 3.35E-03 7.93E-03 1.01E-01 1.01E-01 6.77E-11 5.52E-09 2.66E-02
LERF-Accumulation 2.44E-06 1.05E-01 5.66E-02 3.16E-03 1.38E-04 6.98E-10 1.35E-04 1.27E-04 5.79E-03 4.96E-28 1.31E-32 6.85E-30 2.73E-30 5.57E-07 3.21E-04 4.99E-02 1.03E-37 2.10E-33 8.66E-40 4.44E-10 2.38E-08 2.17E-08 9.22E-10 4.97E-10 3.77E-08 8.99E-07 2.09E-08 2.22E-05 4.79E-06 1.42E-05 3.03E-05 3.79E-04 1.02E-06 6.71E-09 2.18E-05 4.79E-04 3.25E+00 1.47E-03 1.67E-27 1.31E-01 7.19E-03 4.93E-01 4.93E-01 7.39E-30 2.06E-25 2.22E-05
Total Accumulation 4.64E-04 6.82E+01 2.33E+01 2.13E+00 6.15E-01 2.98E+00 3.07E+05 2.90E+05 6.23E-01 3.50E+05 9.34E+01 3.95E+03 1.24E+03 5.46E-04 -5.58E-01 -3.46E+00 5.74E-02 3.78E-01 1.46E-01 5.02E-01 3.19E+01 1.91E+01 8.19E-01 3.31E-01 7.01E+00 1.31E+02 1.84E+01 3.41E+03 7.22E+02 7.32E+03 4.24E+03 8.94E-01 6.75E-02 4.63E+00 1.35E-01 2.46E+00 1.04E+01 1.52E+02 3.40E+02 1.30E+04 4.06E-01 3.89E+06 3.89E+06 3.29E+02 2.89E+02 2.11E+01
Accumulation minus TF and TRU 4.56E-04 3.18E+00 2.25E+00 1.75E-01 5.40E-01 2.95E+00 2.91E+05 2.75E+05 4.12E-01 4.94E+04 1.21E+01 4.43E+02 1.84E+02 2.52E-05 -1.78E-01 -1.61E+00 1.05E-02 5.38E-02 1.35E-02 2.55E-02 1.40E+00 1.39E+00 5.89E-02 3.13E-02 6.43E-01 1.02E+01 1.33E+00 2.54E+02 5.45E+01 7.13E+02 3.48E+02 2.76E-02 3.84E-03 3.21E-01 1.34E-03 2.95E-02 6.80E+00 1.53E+01 3.83E+01 1.36E+03 3.60E-01 2.74E+05 2.74E+05 8.49E+01 7.85E+01 1.31E+01
ADJUSTED INVENTORY TO INCLUDE ACCUMULATION-Radionuclides decayed to 1/1/2008 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
LAW Glass Subtotal (IDF) 1.20E+01 3.32E+03 4.04E+03 3.87E+02 1.65E+01 3.09E-01 1.40E+04 1.32E+04 0.00E+00 2.13E-01 8.41E-05 8.49E-04 1.08E-03 9.23E-03 1.28E+01 1.51E+02 4.06E-08 8.13E-08 9.19E-08 1.46E-01 1.02E+01 2.98E+00 1.21E-01 9.64E-02 1.72E+01 2.38E+02 2.66E+00 4.51E+03 9.64E+02 6.06E+03 7.63E+03 1.21E+02 7.54E-02 3.06E+00 1.33E+01 2.94E+02 0.00E+00 5.03E+01 1.75E-04 4.50E+03 1.41E+02 1.83E+05 1.83E+05 7.76E-04 5.54E-04 9.97E+03
LAW Spent Melter Subtotal (IDF) 1.14E-02 4.28E+00 3.77E+00 4.17E-01 1.64E-02 2.46E-04 1.19E+01 1.13E+01 0.00E+00 2.57E-04 1.02E-07 1.03E-06 1.31E-06 1.04E-05 1.54E-02 1.69E-01 4.90E-11 9.82E-11 1.11E-10 1.28E-04 9.25E-03 3.28E-03 1.33E-04 1.08E-04 1.92E-02 3.02E-01 2.94E-03 5.58E+00 1.19E+00 6.51E+00 9.26E+00 1.13E-01 9.73E-05 3.58E-03 1.31E-02 2.89E-01 0.00E+00 6.09E-02 2.12E-07 5.43E+00 1.58E-01 1.63E+02 1.63E+02 9.39E-07 6.66E-07 1.11E+01
ETF Solid Waste Form to IDF 6.35E-03 1.27E+01 6.94E+01 1.62E+00 6.56E-02 9.68E-06 6.06E-01 5.72E-01 3.67E+00 1.69E-05 4.50E-10 2.07E-07 8.35E-08 1.81E-04 5.94E-02 3.48E+00 3.72E-15 7.55E-11 3.12E-17 3.02E-07 1.79E-05 2.88E-03 1.21E-04 3.37E-05 7.17E-05 3.17E-04 2.77E-03 6.37E-03 1.32E-03 2.12E-02 9.91E-03 4.22E-01 3.47E-04 1.07E-05 4.79E-02 1.05E+00 3.26E+00 1.25E-01 8.65E-05 1.11E+01 2.85E+00 9.37E+01 9.37E+01 2.08E-07 5.80E-03 2.89E-02
Solid Waste Forms from Treatment Processes (IDF) 6.28E-05 7.90E-03 1.30E-02 1.80E-02 1.21E+01 8.22E-02 3.92E+03 3.70E+03 0.00E+00 2.74E-03 6.92E-07 4.15E-05 2.05E-05 3.51E-08 1.42E-06 5.73E-04 1.20E-09 4.06E-09 5.56E-09 2.33E-08 1.68E-06 5.13E-07 2.08E-08 1.59E-08 2.00E-06 1.03E-02 4.61E-07 1.88E-02 1.84E-02 9.93E-03 9.16E-04 3.70E-04 9.03E-09 7.63E-07 6.20E-04 9.94E-04 0.00E+00 4.23E-04 1.72E-05 3.79E-02 5.41E-03 2.63E+01 2.63E+01 2.78E-04 -9.70E-04 1.35E+01
Non-IDF Stream -1.09E-02 4.86E+02 1.38E+00 1.95E-01 6.11E-01 7.13E+02 3.90E+07 3.68E+07 8.24E+02 3.27E+06 8.25E+02 4.95E+04 2.45E+04 1.31E-05 -8.32E+00 -1.46E+02 1.43E+00 4.84E+00 6.63E+00 8.25E+00 6.41E+02 2.16E+02 8.83E+00 6.10E+00 9.12E+01 2.28E+03 1.96E+02 4.37E+04 9.25E+03 1.44E+05 7.23E+04 1.06E-01 6.88E-01 6.49E+01 7.50E-03 1.56E-01 2.81E+03 1.43E+03 3.80E+03 1.28E+05 5.59E-02 4.38E+07 4.38E+07 3.49E+03 2.96E+03 1.65E+04
TOTAL 1.20E+01 3.83E+03 4.11E+03 3.90E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 8.27E+02 3.27E+06 8.25E+02 4.95E+04 2.45E+04 9.43E-03 4.52E+00 8.32E+00 1.43E+00 4.84E+00 6.63E+00 8.39E+00 6.51E+02 2.19E+02 8.95E+00 6.20E+00 1.08E+02 2.52E+03 1.99E+02 4.83E+04 1.02E+04 1.50E+05 8.00E+04 1.21E+02 7.64E-01 6.80E+01 1.34E+01 2.96E+02 2.81E+03 1.48E+03 3.80E+03 1.33E+05 1.44E+02 4.40E+07 4.40E+07 3.49E+03 2.96E+03 2.65E+04
100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 104% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100%
ADJUSTED INVENTORY TO INCLUDE ACCUMULATION-Radionuclides decayed to 1/1/2051 IDF Waste Streams Only 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
LAW Glass Subtotal (IDF) 2.44E-12 4.01E+02 8.17E-02 3.87E+02 1.65E+01 1.66E-07 5.19E+03 4.90E+03 0.00E+00 1.53E-01 9.31E-06 2.65E-05 2.04E-06 9.06E-03 3.25E+00 8.52E-01 4.04E-08 8.13E-08 9.19E-08 9.56E-02 1.02E+01 2.98E+00 1.21E-01 9.64E-02 1.72E+01 1.69E+02 2.66E+00 4.51E+03 9.59E+02 5.87E+03 9.62E+02 9.76E+01 7.54E-02 3.05E+00 4.78E+00 5.67E+01 0.00E+00 5.02E+01 6.14E-07 3.35E+03 1.41E+02 6.51E+04 6.51E+04 7.76E-04 7.41E-04 9.97E+03
LAW Spent Melter Subtotal (IDF) 2.33E-15 5.17E-01 7.64E-05 4.17E-01 1.64E-02 1.32E-10 4.43E+00 4.19E+00 0.00E+00 1.84E-04 1.12E-08 3.20E-08 2.47E-09 1.02E-05 3.92E-03 9.57E-04 4.88E-11 9.82E-11 1.11E-10 8.38E-05 9.25E-03 3.28E-03 1.33E-04 1.08E-04 1.92E-02 2.15E-01 2.94E-03 5.57E+00 1.19E+00 6.33E+00 1.17E+00 9.13E-02 9.73E-05 3.57E-03 4.71E-03 5.57E-02 0.00E+00 6.09E-02 7.42E-10 4.04E+00 1.58E-01 5.79E+01 5.79E+01 9.39E-07 8.96E-07 1.11E+01
ETF Solid Waste Form to IDF 1.29E-15 1.53E+00 1.41E-03 1.62E+00 6.56E-02 5.21E-12 2.25E-01 2.12E-01 3.65E+00 1.21E-05 4.98E-11 6.46E-09 1.57E-10 1.77E-04 1.51E-02 1.97E-02 3.71E-15 7.54E-11 3.12E-17 1.97E-07 1.78E-05 2.88E-03 1.21E-04 3.37E-05 7.17E-05 2.25E-04 2.77E-03 6.36E-03 1.31E-03 2.01E-02 1.25E-03 3.42E-01 3.47E-04 1.07E-05 1.72E-02 2.03E-01 2.90E-01 1.25E-01 3.03E-07 8.28E+00 2.85E+00 3.33E+01 3.33E+01 2.08E-07 9.11E-04 2.89E-02
Solid Waste Forms from Treatment Processes (IDF) 1.28E-17 9.54E-04 2.64E-07 1.80E-02 1.21E+01 4.43E-08 1.45E+03 1.37E+03 0.00E+00 1.97E-03 7.66E-08 1.29E-06 3.87E-08 3.44E-08 3.65E-07 3.25E-06 1.19E-09 4.05E-09 5.56E-09 1.52E-08 1.68E-06 5.12E-07 2.08E-08 1.59E-08 2.00E-06 7.37E-03 4.61E-07 1.88E-02 1.83E-02 9.29E-03 1.16E-04 3.00E-04 9.03E-09 7.60E-07 2.22E-04 1.92E-04 0.00E+00 4.23E-04 6.02E-08 2.82E-02 5.41E-03 9.35E+00 9.35E+00 2.78E-04 8.17E-05 1.35E+01
SSW FRACTIONS BASED ON 10-010 and 10-009 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
HEPA fraction NR NR NR 52% 1.03% 52.45% 50.81% NR 10.40% NR 65.24% 64.99% 65.27% NR NR NR NR NR NR NR 68.98% 68.94% 68.90% 68.85% 54.86% 68.68% 68.39% 68.53% 68.48% 70.74% 68.04% NR NR NR NR NR 0.01% 56.98% 62.75% 57.75% 71.82% 65.75% NR NR NR 87.60%
IX Resin fraction NR NR NR 44% 0.14% 8.96% 9.27% NR 1.53% NR 7.64% 7.67% 7.61% NR NR NR NR NR NR NR 0.00% 0.00% 0.00% 0.00% 42.37% 0.00% 0.00% 0.00% 0.00% 3.83% 0.00% NR NR NR NR NR 49.09% 20.28% 19.08% 19.89% 26.01% 0.09% NR NR NR 11.86%
LAW and HLW Carbon Bed fraction NR NR NR 0% 36.47% 0.00% 0.00% NR 34.07% NR 0.00% 0.00% 0.00% NR NR NR NR NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR NR NR 36.25% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00%
Other Debris fraction NR NR NR 4% 0.01% 38.59% 39.92% NR 24.63% NR 27.13% 27.34% 27.12% NR NR NR NR NR NR NR 31.02% 31.06% 31.10% 31.15% 2.77% 31.32% 31.61% 31.47% 31.52% 25.43% 31.96% NR NR NR NR NR 14.62% 22.75% 18.17% 22.35% 2.17% 34.16% NR NR NR 0.54%
HLW Silver Mordenite Absorbent fraction NR NR NR 0% 62.35% 0.00% 0.00% NR 29.36% NR 0.00% 0.00% 0.00% NR NR NR NR NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR NR NR 0.03% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00%
WTP SSW INVENTORY-Radionuclides decayed to 1/1/2008 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
HEPA Filters Debris NR NR NR 9.35E-03 1.25E-01 4.31E-02 1.99E+03 NR 0.00E+00 NR 4.51E-07 2.70E-05 1.34E-05 NR NR NR NR NR NR NR 1.16E-06 3.53E-07 1.43E-08 1.09E-08 1.10E-06 7.11E-03 3.15E-07 1.29E-02 1.26E-02 7.02E-03 6.23E-04 NR NR NR NR NR 0.00E+00 2.41E-04 1.08E-05 2.19E-02 3.88E-03 1.73E+01 NR NR NR 1.18E+01
IX Resin Non-Debris NR NR NR 7.90E-03 1.66E-02 7.37E-03 3.63E+02 NR 0.00E+00 NR 5.29E-08 3.18E-06 1.56E-06 NR NR NR NR NR NR NR 5.64E-13 1.77E-13 6.10E-15 7.46E-15 8.49E-07 7.49E-08 1.61E-13 1.37E-07 1.35E-07 3.80E-04 6.78E-09 NR NR NR NR NR 0.00E+00 8.58E-05 3.28E-06 7.54E-03 1.41E-03 2.47E-02 NR NR NR 1.60E+00
LAW and HLW Carbon Beds Non-Debris NR NR NR 1.87E-13 4.42E+00 1.53E-11 6.18E-07 NR 0.00E+00 NR 1.43E-18 8.93E-17 4.37E-17 NR NR NR NR NR NR NR 6.29E-19 2.12E-19 8.89E-21 8.47E-21 2.02E-17 3.98E-15 1.93E-19 7.30E-15 7.13E-15 1.32E-14 3.59E-16 NR NR NR NR NR 0.00E+00 1.76E-14 1.11E-16 1.57E-12 3.94E-13 3.06E-09 NR NR NR 1.78E-09
Other Debris Debris NR NR NR 7.91E-04 1.09E-03 3.17E-02 1.56E+03 NR 0.00E+00 NR 1.88E-07 1.14E-05 5.57E-06 NR NR NR NR NR NR NR 5.22E-07 1.59E-07 6.47E-09 4.95E-09 5.55E-08 3.24E-03 1.46E-07 5.92E-03 5.81E-03 2.52E-03 2.93E-04 NR NR NR NR NR 0.00E+00 9.63E-05 3.13E-06 8.47E-03 1.17E-04 9.00E+00 NR NR NR 7.27E-02
HLW Silver Mordenite Absorbent Non-Debris NR NR NR 1.81E-16 7.56E+00 3.05E-11 1.23E-06 NR 0.00E+00 NR 3.60E-19 2.75E-17 1.32E-17 NR NR NR NR NR NR NR 1.26E-18 4.24E-19 1.78E-20 1.69E-20 1.31E-20 7.96E-15 3.87E-19 1.46E-14 1.42E-14 7.79E-15 7.18E-16 NR NR NR NR NR 0.00E+00 2.84E-14 2.38E-17 2.54E-12 4.83E-14 6.11E-09 NR NR NR 1.50E-12
SSW Total NR NR NR 1.80E-02 1.21E+01 8.22E-02 3.92E+03 NR 0.00E+00 NR 6.92E-07 4.15E-05 2.05E-05 NR NR NR NR NR NR NR 1.68E-06 5.13E-07 2.08E-08 1.59E-08 2.00E-06 1.03E-02 4.61E-07 1.88E-02 1.84E-02 9.93E-03 9.16E-04 NR NR NR NR NR 0.00E+00 4.23E-04 1.72E-05 3.79E-02 5.41E-03 2.63E+01 NR NR NR 1.35E+01
BBI 2.94E+01 3.90E+07 4.76E+07 2.65E+04
Check N/A N/A N/A 100% 100% 100% 100% N/A #DIV/0! N/A 100% 100% 100% N/A N/A N/A N/A N/A N/A N/A 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% N/A N/A N/A N/A N/A #DIV/0! 100% 100% 100% 100% 100% N/A N/A N/A 100%
WTP SSW INVENTORY-Radionuclides decayed to 1/1/2051 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
HEPA Filters Debris NR NR NR 9.35E-03 1.25E-01 2.32E-08 7.39E+02 NR 0.00E+00 0.00E+00 5.00E-08 8.41E-07 2.52E-08 NR NR NR NR NR NR NR 1.16E-06 3.53E-07 1.43E-08 1.09E-08 1.10E-06 5.06E-03 3.15E-07 1.29E-02 1.26E-02 6.57E-03 7.86E-05 NR NR NR NR NR 0.00E+00 2.41E-04 3.78E-08 1.63E-02 3.88E-03 6.15E+00 NR NR NR 1.18E+01
IX Resin Non-Debris NR NR NR 7.90E-03 1.66E-02 3.97E-09 1.35E+02 NR 0.00E+00 0.00E+00 5.85E-09 9.92E-08 2.94E-09 NR NR NR NR NR NR NR 5.64E-13 1.77E-13 6.10E-15 7.46E-15 8.49E-07 5.33E-08 1.61E-13 1.37E-07 1.34E-07 3.54E-04 8.55E-10 NR NR NR NR NR 0.00E+00 8.58E-05 1.15E-08 5.61E-03 1.41E-03 8.77E-03 NR NR NR 1.60E+00
LAW and HLW Carbon Beds Non-Debris NR NR NR 1.87E-13 4.42E+00 8.26E-18 2.29E-07 NR 0.00E+00 0.00E+00 1.58E-19 2.78E-18 8.23E-20 NR NR NR NR NR NR NR 6.29E-19 2.12E-19 8.89E-21 8.47E-21 2.02E-17 2.84E-15 1.93E-19 7.29E-15 7.09E-15 1.23E-14 4.53E-17 NR NR NR NR NR 0.00E+00 1.76E-14 3.90E-19 1.17E-12 3.93E-13 1.08E-09 NR NR NR 1.78E-09
Other Debris Debris NR NR NR 7.91E-04 1.09E-03 1.71E-08 5.81E+02 NR 0.00E+00 0.00E+00 2.08E-08 3.54E-07 1.05E-08 NR NR NR NR NR NR NR 5.22E-07 1.59E-07 6.47E-09 4.95E-09 5.55E-08 2.31E-03 1.46E-07 5.91E-03 5.78E-03 2.36E-03 3.69E-05 NR NR NR NR NR 0.00E+00 9.63E-05 1.09E-08 6.31E-03 1.17E-04 3.20E+00 NR NR NR 7.27E-02
HLW Silver Mordenite Absorbent Non-Debris NR NR NR 1.81E-16 7.56E+00 1.64E-17 4.55E-07 NR 0.00E+00 0.00E+00 3.98E-20 8.56E-19 2.48E-20 NR NR NR NR NR NR NR 1.26E-18 4.24E-19 1.78E-20 1.69E-20 1.31E-20 5.67E-15 3.87E-19 1.46E-14 1.42E-14 7.29E-15 9.06E-17 NR NR NR NR NR 0.00E+00 2.83E-14 8.33E-20 1.89E-12 4.83E-14 2.17E-09 NR NR NR 1.50E-12SE
CT
ION
5B
SE
CT
ION
1S
EC
TIO
N 2
SE
CT
ION
3A
SE
CT
ION
4S
EC
TIO
N 5
AS
EC
TIO
N 3
B
RPP-ENV-58562 Rev.03 5/9/2016 - 11:21 AM 102 of 118RPP-ENV-58562 Rev.03 9/26/2016 - 12:49 PM 102 of 124
RPP-ENV-58562, Rev. 3
A-9/A-10
Table A-4. Run Case 8B Chemicals.
SVF-4094, IDF PA Case 8B - Tc_Tc-99 Removal from LAW Vitrification Off-Gas Condensate - Mass Balance, MMR-50051
WASTE STREAM Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
LAW Glass Subtotal (IDF) 1.09E+03 2.38E+07 4.67E+03 2.25E+07 1.04E+01 4.96E+02 6.37E+04 5.23E+03 5.03E+04 7.36E+05 4.91E+05 7.44E-01 3.58E+02 1.11E+06 2.85E+07 0.00E+00 9.38E+05 6.67E-05 8.02E+06 6.59E+06 6.81E-05 6.49E+03 8.01E+07 3.18E+03 2.15E+03 0.00E+00 0.00E+00 0.00E+00 6.92E+04 2.12E+03 0.00E+00 0.00E+00 7.66E+01 2.74E+02 0.00E+00 3.07E+03 3.48E+03 5.03E+03 1.62E+08 0.00E+00 3.14E+06 0.00E+00 4.61E+01 6.94E-02 5.88E+02 1.64E+03 8.33E-04 8.83E+06 2.28E-04 0.00E+00 7.93E+03 7.48E-01 4.14E+03 8.77E+01 1.75E+07 1.63E+07
LAW Spent Melter Subtotal (IDF) 1.36E+00 2.77E+04 5.11E+00 2.61E+04 1.46E-02 5.57E-01 7.73E+01 6.15E+00 5.93E+01 7.74E+02 5.71E+02 6.43E-04 4.17E-01 1.27E+03 3.31E+04 0.00E+00 1.25E+03 8.05E-08 8.47E+03 7.65E+03 8.23E-08 7.08E+00 9.58E+04 3.90E+00 2.66E+00 0.00E+00 0.00E+00 0.00E+00 7.01E+01 1.66E+00 0.00E+00 0.00E+00 9.48E-02 2.69E-01 0.00E+00 2.37E+00 3.77E+00 5.50E+00 1.87E+05 0.00E+00 3.58E+03 0.00E+00 4.50E-02 9.26E-05 6.57E-01 2.12E+00 1.01E-06 1.03E+04 2.55E-07 1.38E-02 8.75E+00 9.14E-04 2.56E+00 1.13E-01 2.03E+04 1.89E+04
ETF Solid Waste Form to IDF 2.98E+00 1.84E+01 9.76E+01 6.53E+01 6.73E-01 2.38E+00 3.20E+02 5.46E-01 1.11E+03 8.80E+02 4.32E+00 3.24E-05 3.47E+00 4.80E+03 2.96E+02 9.37E+02 6.84E+00 2.73E-03 8.60E+00 1.14E+00 3.38E+01 3.01E+01 3.50E+05 1.10E+01 6.05E+00 4.64E+01 1.64E+05 1.30E+05 9.57E+03 5.72E+00 2.39E+02 0.00E+00 1.95E-04 8.89E-01 0.00E+00 7.19E+00 7.19E+01 1.02E+02 2.16E+03 0.00E+00 0.00E+00 1.77E+03 1.09E+01 6.06E-04 1.71E-03 4.46E+01 2.83E-13 1.07E-05 1.45E-05 8.23E+03 8.26E+00 3.00E-05 4.62E-03 2.43E-03 2.69E+01 1.42E-05
Solid Waste Forms from Treatment Processes (IDF) 1.01E-01 2.19E+01 2.82E-01 2.88E+01 3.71E-02 5.56E-05 2.41E-02 3.37E-01 7.73E-04 8.00E+04 7.43E+02 2.06E-01 3.24E-03 1.05E+05 1.31E-01 9.97E+02 3.11E+02 8.77E-07 1.14E-01 8.90E-03 8.43E-02 1.41E-02 4.65E+03 3.06E-05 5.86E-01 0.00E+00 0.00E+00 0.00E+00 1.17E+01 2.38E-04 4.00E+03 6.67E-07 3.83E-04 1.05E-03 7.77E-07 8.14E-03 1.13E-02 4.78E-01 2.04E-01 5.90E+03 0.00E+00 0.00E+00 3.62E-02 2.19E-07 7.97E-01 2.71E-02 5.05E-05 2.85E-04 1.46E-04 0.00E+00 1.37E-03 2.84E-05 4.64E-04 2.67E-06 1.55E-01 3.23E-02
Non-IDF Stream 2.70E+03 2.47E+06 8.96E+01 1.54E+06 8.64E+03 2.84E+00 4.81E+05 3.43E+03 6.57E+03 4.96E+03 6.90E+04 2.07E+03 2.35E+03 3.28E+04 1.45E+06 1.43E+01 1.56E+04 4.21E+04 7.39E+05 2.29E+04 4.62E+05 2.42E+01 1.87E+06 6.02E+03 1.17E+05 1.69E+07 5.95E+07 2.63E+07 2.74E+03 9.28E-01 5.13E+06 7.95E+02 7.42E+02 1.54E-01 9.27E+02 9.62E-01 1.59E+02 3.44E+01 5.37E+06 -5.90E+03 -3.14E+06 3.80E+06 6.19E+04 2.51E+02 9.72E+02 1.22E+03 6.02E+04 1.38E+03 6.66E+03 8.61E+05 5.84E+05 2.38E+03 1.27E+01 4.76E+02 4.32E+02 4.06E+05
BBI 4.03E+03 8.67E+06 4.88E+03 1.52E+04 9.42E+03 5.02E+02 5.61E+05 8.87E+03 6.96E+03 8.27E+05 5.91E+05 2.09E+03 2.91E+03 1.28E+06 1.27E+06 1.99E+03 9.57E+05 3.20E+04 1.94E+03 2.19E+04 1.64E+05 6.56E+03 4.92E+07 9.70E+03 9.87E+04 1.19E+07 5.60E+07 4.45E+06 8.20E+04 2.14E+03 5.18E+06 8.43E+02 8.45E+02 2.78E+02 9.47E+02 3.09E+03 3.73E+03 5.18E+03 8.41E+05 0.00E+00 0.00E+00 3.82E+06 4.23E+04 2.72E+02 1.56E+03 2.92E+03 6.15E+04 1.51E+03 6.98E+03 8.71E+05 6.45E+05 2.58E+03 4.16E+03 5.81E+02 6.08E+03 4.09E+05
HTWOS Feed 4.03E+03 2.68E+07 4.88E+03 2.40E+07 9.42E+03 5.02E+02 6.02E+05 8.87E+03 5.88E+04 8.28E+05 5.91E+05 2.09E+03 2.91E+03 1.28E+06 3.01E+07 1.99E+03 9.57E+05 4.47E+04 8.76E+06 6.62E+06 4.79E+05 6.56E+03 8.26E+07 9.70E+03 1.25E+05 1.69E+07 5.98E+07 2.64E+07 8.20E+04 2.14E+03 5.20E+06 8.43E+02 8.77E+02 2.78E+02 9.47E+02 3.09E+03 3.73E+03 5.18E+03 1.68E+08 0.00E+00 0.00E+00 3.83E+06 6.51E+04 2.72E+02 1.56E+03 2.92E+03 6.15E+04 8.84E+06 6.98E+03 8.71E+05 6.47E+05 2.58E+03 4.16E+03 5.81E+02 1.75E+07 1.67E+07
HTWOS Feed Adjusted Minus TF and TRU Accumulation 3.82E+03 2.63E+07 4.87E+03 2.40E+07 8.70E+03 5.02E+02 5.46E+05 8.67E+03 5.84E+04 8.28E+05 5.63E+05 2.09E+03 2.73E+03 1.28E+06 3.00E+07 1.97E+03 9.56E+05 4.22E+04 8.76E+06 6.62E+06 4.67E+05 6.55E+03 8.25E+07 9.26E+03 1.20E+05 1.69E+07 5.98E+07 2.64E+07 8.16E+04 2.13E+03 5.14E+06 8.23E+02 8.23E+02 2.75E+02 9.39E+02 3.08E+03 3.72E+03 5.18E+03 1.68E+08 0.00E+00 0.00E+00 3.82E+06 6.22E+04 2.66E+02 1.56E+03 2.91E+03 6.03E+04 8.84E+06 6.80E+03 8.70E+05 5.96E+05 2.40E+03 4.15E+03 5.70E+02 1.75E+07 1.67E+07
ACCUMULATION STREAM Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
PT-Accumulation 3.09E+01 2.45E+04 3.35E+00 4.19E+00 4.87E+01 1.69E-01 1.60E+03 1.48E+00 4.12E+02 4.86E+02 1.75E+03 1.53E+01 1.28E+01 2.14E+03 5.37E+03 1.06E+00 3.37E+02 4.20E+01 5.42E-01 1.85E+02 4.61E+03 2.10E+00 4.22E+04 3.78E+01 4.47E+02 5.62E+03 5.02E+04 8.77E+03 4.67E+01 3.91E-02 3.03E+03 2.59E+01 4.04E+00 1.67E-02 1.20E+01 4.95E-02 1.54E+00 2.76E+00 4.37E+03 0.00E+00 0.00E+00 3.64E+03 1.52E+02 1.38E+01 4.92E-01 6.36E-01 1.15E+02 1.38E+01 1.35E+02 4.31E+02 3.73E+03 2.19E+01 5.83E-02 5.32E+00 1.93E+00 5.58E+02
TF-Accumulation 2.04E+02 4.63E+05 4.23E+00 2.53E+01 7.18E+02 3.32E-01 5.49E+04 1.99E+02 4.11E+02 5.97E+02 2.74E+04 9.07E-01 1.85E+02 6.38E+03 1.11E+05 1.73E+01 4.55E+02 2.49E+03 2.69E+00 1.67E+03 1.21E+04 3.50E+00 9.10E+04 4.49E+02 5.71E+03 6.42E+03 4.19E+04 6.24E+03 4.18E+02 7.34E+00 6.52E+04 2.03E+01 5.37E+01 3.50E+00 7.91E+00 5.07E+00 2.75E+00 2.71E+00 6.89E+04 0.00E+00 0.00E+00 2.66E+03 2.93E+03 5.68E+00 4.73E-01 3.00E+00 1.20E+03 1.15E+02 1.81E+02 7.69E+02 5.13E+04 1.78E+02 2.71E+00 1.08E+01 1.93E+01 1.79E+03
TRU-Accumulation 1.94E-02 2.91E+02 1.35E-02 2.92E-01 1.55E-01 6.08E-03 3.38E+02 9.73E-02 3.47E+00 1.25E+01 1.62E+01 1.47E-04 9.11E-01 1.57E+02 1.61E+02 2.34E-03 1.66E+00 1.96E-02 7.92E-115 2.52E+00 1.11E+00 3.96E-114 1.31E+03 7.92E-114 2.02E-01 3.37E+02 1.08E+03 1.08E-01 9.32E-01 0.00E+00 1.34E+03 0.00E+00 3.72E-02 0.00E+00 0.00E+00 1.13E-20 7.22E-01 8.75E-03 1.17E+02 0.00E+00 0.00E+00 7.15E+01 1.80E+00 0.00E+00 6.93E-04 0.00E+00 1.77E-08 1.73E-01 8.36E-113 5.54E+00 1.61E+01 2.50E-62 3.60E-299 6.08E-08 2.55E+00 1.21E+00
LAW Accumulation 4.21E-01 1.43E+03 6.50E-01 9.40E+02 1.80E-03 2.81E-02 8.29E+00 2.96E-01 1.31E+00 1.04E+02 7.06E+01 3.16E-05 8.41E-03 4.63E+02 1.20E+03 1.85E-01 4.36E+01 1.71E-250 9.64E-02 2.76E+02 1.75E-250 3.67E-01 9.04E+03 5.64E-01 6.94E-01 5.80E+02 2.98E+03 2.05E+03 6.03E+00 7.56E-03 3.59E+02 0.00E+00 1.11E-02 3.28E-03 0.00E+00 8.73E-03 2.74E-01 4.91E-01 6.35E+03 8.94E-02 1.02E+02 5.45E+02 9.58E-03 1.38E-05 1.23E-01 1.33E-01 2.15E-249 3.69E+02 1.09E-198 4.48E+01 6.54E-01 9.62E-05 1.16E-02 1.76E-02 7.31E+02 6.83E+02
HLW-Accumulation 1.56E+00 1.33E+03 1.34E-03 8.38E+02 3.53E+00 2.85E-05 8.86E+01 1.51E-03 5.75E+00 1.03E-02 5.35E+01 3.51E-01 8.69E-01 5.44E-02 3.75E+02 6.56E-04 2.01E+00 3.03E+00 3.76E+02 1.32E+01 3.44E+02 6.52E-04 4.37E+02 2.08E+00 3.10E+01 1.73E+00 1.36E+02 8.99E+00 8.53E-02 2.82E-05 9.12E-02 1.90E+00 2.70E-01 1.16E-05 8.90E-01 1.58E-05 2.30E-04 3.03E-04 2.37E+03 6.51E-05 3.88E-02 5.68E-02 9.73E+00 1.01E+00 1.79E-05 3.58E-04 7.88E+00 1.01E+00 6.03E+00 4.33E-02 2.53E+02 1.51E+00 4.44E-05 3.91E-01 2.61E-04 4.10E+01
SLAW-Accumulation 7.79E-01 1.59E+03 1.13E+01 9.10E+02 4.14E-03 4.26E-02 2.34E+01 7.64E-01 5.77E+00 4.84E+03 5.37E+02 4.38E-04 7.43E-02 2.19E+04 1.16E+03 2.45E+01 2.89E+02 1.16E-25 2.13E-01 2.67E+02 1.18E-25 1.00E+00 4.76E+04 9.75E-01 9.91E-01 7.30E+02 1.59E+04 2.94E+03 7.33E+00 2.53E-02 1.48E+03 0.00E+00 1.90E-02 1.46E-02 0.00E+00 1.79E-02 2.66E+00 5.10E+00 6.15E+03 1.05E-01 9.63E+01 1.39E+04 1.87E-02 3.15E-05 1.54E-01 3.02E+00 1.45E-24 3.58E+02 8.69E-16 4.65E+01 1.30E+00 2.96E-04 3.48E-02 3.05E-02 7.09E+02 6.61E+02
LAWPS-Accumulation 6.49E-06 2.77E-01 2.07E-03 9.07E-03 8.74E-06 1.14E-03 2.92E-02 3.03E-04 0.00E+00 3.20E-01 1.24E-01 1.02E-03 1.94E-04 1.15E+00 1.01E-02 1.78E-03 5.00E-01 0.00E+00 1.51E-03 0.00E+00 0.00E+00 2.95E-03 2.85E+01 2.69E-04 6.19E-06 8.77E+00 3.29E+01 2.04E+00 8.46E-02 4.32E-04 2.56E+00 0.00E+00 9.45E-07 1.11E-05 0.00E+00 4.62E-04 2.05E-03 3.62E-03 1.42E-01 0.00E+00 0.00E+00 4.74E+00 1.40E-05 3.49E-08 4.93E-04 2.64E-03 0.00E+00 0.00E+00 0.00E+00 4.35E-01 1.59E-03 3.75E-07 1.81E-04 8.37E-06 6.60E-03 0.00E+00
ETF-Accumulation 3.53E-04 2.88E-01 1.70E-01 8.24E-03 6.64E-07 3.18E-04 3.05E-02 8.73E-04 3.03E-10 7.09E+01 1.12E+00 9.67E-06 4.51E-03 2.27E+01 2.21E-03 9.58E-02 2.26E+01 2.70E-10 1.13E-03 9.02E-12 2.76E-10 1.35E-02 1.87E+02 7.18E-04 1.17E-03 5.17E+00 1.97E+02 1.74E+00 5.71E-02 3.77E-03 1.62E+00 0.00E+00 5.85E-06 1.35E-03 0.00E+00 8.68E-03 1.35E-01 2.61E-01 6.03E-03 0.00E+00 0.00E+00 6.37E+01 1.99E-05 2.45E-09 1.57E-03 5.28E-03 3.43E-09 1.57E-11 3.08E-08 0.00E+00 2.96E-03 8.28E-07 6.46E-03 3.08E-05 7.59E-04 2.59E-11
LERF-Accumulation 2.67E-02 3.68E-03 3.41E-01 8.58E-02 2.59E-04 3.22E-03 1.84E+00 2.16E-03 4.10E+00 1.31E+00 2.84E-02 7.34E-09 2.95E-03 2.29E+01 1.56E+00 7.10E-01 9.74E-03 2.41E-27 2.24E-02 8.21E-24 3.25E-23 7.53E-02 1.62E+03 7.81E-02 4.61E-02 1.72E-03 3.42E+02 1.31E+03 1.33E+01 3.00E-03 8.62E-02 0.00E+00 6.37E-07 1.32E-03 0.00E+00 1.99E-03 6.85E-02 1.23E-01 3.75E+00 0.00E+00 0.00E+00 3.45E+00 4.97E-02 6.88E-06 1.31E-06 1.05E-01 7.87E-36 6.88E-29 2.41E-31 1.85E+01 6.27E-05 3.00E-05 4.62E-03 2.43E-03 2.81E-02 4.88E-28
Total Accumulation 2.38E+02 4.92E+05 2.01E+01 2.72E+03 7.70E+02 5.82E-01 5.70E+04 2.02E+02 8.43E+02 6.11E+03 2.98E+04 1.66E+01 1.99E+02 3.11E+04 1.19E+05 4.39E+01 1.15E+03 2.54E+03 3.80E+02 2.41E+03 1.70E+04 7.06E+00 1.93E+05 4.90E+02 6.19E+03 1.37E+04 1.13E+05 2.13E+04 4.92E+02 7.42E+00 7.14E+04 4.81E+01 5.81E+01 3.53E+00 2.08E+01 5.16E+00 8.16E+00 1.15E+01 8.83E+04 1.94E-01 1.98E+02 2.09E+04 3.09E+03 2.05E+01 1.24E+00 6.90E+00 1.33E+03 8.57E+02 3.22E+02 1.32E+03 5.53E+04 2.01E+02 2.82E+00 1.66E+01 1.46E+03 3.74E+03
Accumulation minus TF and TRU 3.37E+01 2.89E+04 1.58E+01 2.69E+03 5.22E+01 2.44E-01 1.72E+03 2.54E+00 4.29E+02 5.50E+03 2.42E+03 1.57E+01 1.38E+01 2.46E+04 8.11E+03 2.66E+01 6.95E+02 4.50E+01 3.77E+02 7.41E+02 4.95E+03 3.56E+00 1.01E+05 4.15E+01 4.80E+02 6.94E+03 6.98E+04 1.51E+04 7.35E+01 7.92E-02 4.87E+03 2.78E+01 4.33E+00 3.73E-02 1.29E+01 8.73E-02 4.68E+00 8.74E+00 1.92E+04 1.94E-01 1.98E+02 1.81E+04 1.62E+02 1.48E+01 7.71E-01 3.91E+00 1.23E+02 7.42E+02 1.41E+02 5.41E+02 3.99E+03 2.34E+01 1.16E-01 5.76E+00 1.44E+03 1.94E+03
ADJUSTED INVENTORY TO INCLUDE ACCUMULATION Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
LAW Glass Subtotal (IDF) 1.10E+03 2.38E+07 4.68E+03 2.25E+07 1.05E+01 4.96E+02 6.39E+04 5.24E+03 5.06E+04 7.40E+05 4.93E+05 7.50E-01 3.60E+02 1.13E+06 2.85E+07 0.00E+00 9.39E+05 6.68E-05 8.02E+06 6.59E+06 6.89E-05 6.49E+03 8.02E+07 3.19E+03 2.16E+03 0.00E+00 0.00E+00 0.00E+00 6.92E+04 2.12E+03 0.00E+00 0.00E+00 7.70E+01 2.74E+02 0.00E+00 3.07E+03 3.49E+03 5.04E+03 1.62E+08 #DIV/0! #DIV/0! 0.00E+00 4.62E+01 7.33E-02 5.88E+02 1.64E+03 8.35E-04 8.83E+06 2.32E-04 0.00E+00 7.99E+03 7.55E-01 4.14E+03 8.86E+01 1.75E+07 1.63E+07
LAW Spent Melter Subtotal (IDF) 1.38E+00 2.77E+04 5.12E+00 2.61E+04 1.47E-02 5.58E-01 7.76E+01 6.16E+00 5.97E+01 7.79E+02 5.73E+02 6.48E-04 4.19E-01 1.29E+03 3.31E+04 0.00E+00 1.25E+03 8.06E-08 8.47E+03 7.65E+03 8.32E-08 7.09E+00 9.59E+04 3.92E+00 2.67E+00 0.00E+00 0.00E+00 0.00E+00 7.02E+01 1.66E+00 0.00E+00 0.00E+00 9.53E-02 2.69E-01 0.00E+00 2.37E+00 3.77E+00 5.51E+00 1.87E+05 #DIV/0! #DIV/0! 0.00E+00 4.51E-02 9.78E-05 6.57E-01 2.12E+00 1.01E-06 1.03E+04 2.61E-07 1.38E-02 8.81E+00 9.22E-04 2.56E+00 1.14E-01 2.03E+04 1.89E+04
ETF Solid Waste Form to IDF 3.00E+00 1.85E+01 9.79E+01 6.53E+01 6.77E-01 2.38E+00 3.21E+02 5.46E-01 1.12E+03 8.86E+02 4.34E+00 3.26E-05 3.49E+00 4.89E+03 2.96E+02 9.50E+02 6.85E+00 2.74E-03 8.60E+00 1.14E+00 3.42E+01 3.01E+01 3.51E+05 1.11E+01 6.07E+00 4.64E+01 1.64E+05 1.31E+05 9.58E+03 5.72E+00 2.39E+02 0.00E+00 1.96E-04 8.89E-01 0.00E+00 7.19E+00 7.20E+01 1.02E+02 2.16E+03 #DIV/0! #DIV/0! 1.78E+03 1.09E+01 6.40E-04 1.71E-03 4.46E+01 2.84E-13 1.07E-05 1.48E-05 8.23E+03 8.31E+00 3.03E-05 4.62E-03 2.45E-03 2.69E+01 1.42E-05
Solid Waste Forms from Treatment Processes (IDF) 1.02E-01 2.20E+01 2.83E-01 2.88E+01 3.73E-02 5.56E-05 2.42E-02 3.37E-01 7.79E-04 8.06E+04 7.46E+02 2.08E-01 3.26E-03 1.07E+05 1.31E-01 1.01E+03 3.12E+02 8.78E-07 1.14E-01 8.90E-03 8.52E-02 1.41E-02 4.66E+03 3.08E-05 5.88E-01 0.00E+00 0.00E+00 0.00E+00 1.18E+01 2.38E-04 4.00E+03 6.90E-07 3.85E-04 1.05E-03 7.88E-07 8.14E-03 1.13E-02 4.78E-01 2.04E-01 #DIV/0! #DIV/0! 0.00E+00 3.63E-02 2.31E-07 7.97E-01 2.71E-02 5.06E-05 2.85E-04 1.49E-04 0.00E+00 1.38E-03 2.87E-05 4.64E-04 2.69E-06 1.55E-01 3.23E-02
Non-IDF Stream 2.72E+03 2.47E+06 8.99E+01 1.54E+06 8.69E+03 2.84E+00 4.82E+05 3.43E+03 6.62E+03 5.00E+03 6.93E+04 2.09E+03 2.36E+03 3.35E+04 1.46E+06 1.45E+01 1.56E+04 4.22E+04 7.39E+05 2.29E+04 4.67E+05 2.43E+01 1.88E+06 6.05E+03 1.17E+05 1.69E+07 5.96E+07 2.63E+07 2.74E+03 9.28E-01 5.13E+06 8.22E+02 7.46E+02 1.54E-01 9.39E+02 9.62E-01 1.59E+02 3.45E+01 5.37E+06 #DIV/0! #DIV/0! 3.82E+06 6.21E+04 2.65E+02 9.72E+02 1.23E+03 6.03E+04 1.38E+03 6.79E+03 8.62E+05 5.88E+05 2.40E+03 1.27E+01 4.81E+02 4.32E+02 4.06E+05
TOTAL 3.82E+03 2.63E+07 4.87E+03 2.40E+07 8.70E+03 5.02E+02 5.46E+05 8.67E+03 5.84E+04 8.28E+05 5.63E+05 2.09E+03 2.73E+03 1.28E+06 3.00E+07 1.97E+03 9.56E+05 4.22E+04 8.76E+06 6.62E+06 4.67E+05 6.55E+03 8.25E+07 9.26E+03 1.20E+05 1.69E+07 5.98E+07 2.64E+07 8.16E+04 2.13E+03 5.14E+06 8.22E+02 8.23E+02 2.75E+02 9.39E+02 3.08E+03 3.72E+03 5.18E+03 1.68E+08 #DIV/0! #DIV/0! 3.82E+06 6.22E+04 2.65E+02 1.56E+03 2.91E+03 6.03E+04 8.84E+06 6.79E+03 8.70E+05 5.96E+05 2.40E+03 4.15E+03 5.70E+02 1.75E+07 1.67E+07
100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% #DIV/0! #DIV/0! 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100%
SSW FRACTIONS BASED ON 10-010 and 10-009 Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
HEPA fraction 4.53% 17.39% 17.89% 62.10% 6.43% 0.15% 5.17% 50.79% 0.21% 0.00% 94.18% NR 0.00% 0.00% 44.22% 0.00% 56.46% 7.86% 91.84% 69.10% 12.79% NR 40.68% 4.20% 13.13% NR NR NR 61.05% 1.03% NR #DIV/0! 8.09% 5.61% 5.04% 78.35% 5.42% 31.35% 41.49% NR NR NR 15.98% 0.00% 63.36% 20.43% 7.69% 71.77% 23.04% NR 8.06% 41% 0% NR 87% 61%
IX Resin fraction 43.06% 62.12% 53.58% 0.54% 22.10% 93.91% 29.47% 23.43% 90.28% 95.63% 5.35% NR 0.00% 0.08% 0.00% 0.00% 42.37% 5.18% 0.04% 0.12% 0.00% NR 55.24% 45.56% 38.04% NR NR NR 19.53% 83.67% NR #DIV/0! 0.00% 61.81% 76.38% 0.00% 72.52% 63.57% 0.12% NR NR NR 0.23% 0.00% 34.99% 4.19% 25.51% 0.00% 38.40% NR 0.00% 17% 94% NR 0% 0%
LAW and HLW Carbon Bed fraction 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 98.32% 0.00% 100.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% NR #DIV/0! 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0% 0% NR 0% 0%
Other Debris fraction 52.41% 20.48% 28.53% 37.37% 71.47% 5.95% 65.36% 25.78% 9.52% 4.37% 0.47% NR 100.00% 0.01% 55.78% 0.00% 1.17% 86.96% 8.12% 30.78% 87.21% NR 4.08% 50.24% 48.83% NR NR NR 19.42% 15.31% NR #DIV/0! 91.91% 32.59% 18.58% 21.65% 22.06% 5.08% 58.40% NR NR NR 83.79% 100.00% 1.65% 75.39% 66.80% 28.23% 38.56% NR 91.94% 42% 6% NR 13% 39%
HLW Silver Mordenite Absorbent fraction 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 1.59% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% NR #DIV/0! 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0% 0% NR 0% 0%
WTP SSW INVENTORY Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
HEPA Filters Debris 4.63E-03 3.82E+00 5.06E-02 1.79E+01 2.40E-03 8.12E-08 1.25E-03 1.71E-01 1.61E-06 0.00E+00 7.03E+02 NR 0.00E+00 1.69E-01 5.81E-02 0.00E+00 1.76E+02 6.90E-08 1.05E-01 6.15E-03 1.09E-02 NR 1.89E+03 1.29E-06 7.72E-02 NR NR NR 7.17E+00 2.45E-06 NR #DIV/0! 3.11E-05 5.91E-05 3.97E-08 6.38E-03 6.11E-04 1.50E-01 8.45E-02 NR NR NR 5.81E-03 0.00E+00 5.05E-01 5.54E-03 3.89E-06 2.05E-04 3.42E-05 NR 1.11E-04 1.18E-05 1.05E-06 NR 1.36E-01 1.96E-02
IX Resin Non-Debris 4.40E-02 1.36E+01 1.52E-01 1.54E-01 8.25E-03 5.22E-05 7.14E-03 7.90E-02 7.03E-04 7.71E+04 3.99E+01 NR 0.00E+00 8.99E+01 5.23E-07 2.26E-02 1.32E+02 4.55E-08 4.15E-05 1.03E-05 1.88E-08 NR 2.57E+03 1.40E-05 2.24E-01 NR NR NR 2.30E+00 1.99E-04 NR #DIV/0! 8.02E-09 6.52E-04 6.02E-07 1.20E-08 8.17E-03 3.04E-01 2.42E-04 NR NR NR 8.34E-05 0.00E+00 2.79E-01 1.13E-03 1.29E-05 4.95E-12 5.71E-05 NR 1.37E-09 4.77E-06 4.36E-04 NR 1.21E-05 1.23E-04
LAW and HLW Carbon Beds Non-Debris 1.18E-12 2.57E-09 7.12E-11 1.33E-08 3.24E-13 1.24E-15 1.97E-13 2.56E-10 1.62E-14 4.23E-02 7.29E-10 NR 0.00E+00 1.05E+05 3.46E-11 1.01E+03 1.07E-07 1.52E-18 6.30E-11 3.70E-12 1.09E-11 NR 1.20E-06 3.31E-16 6.92E-11 NR NR NR 5.33E-09 4.76E-15 NR #DIV/0! 4.31E-16 3.36E-14 3.16E-17 1.82E-11 7.37E-13 1.58E-10 5.07E-11 NR NR NR 1.03E-11 0.00E+00 3.12E-10 9.07E-12 1.06E-15 1.23E-13 1.59E-14 NR 1.56E-15 7.04E-15 1.03E-14 NR 8.10E-11 1.18E-11
Other Debris Debris 5.36E-02 4.50E+00 8.07E-02 1.08E+01 2.67E-02 3.31E-06 1.58E-02 8.70E-02 7.41E-05 3.52E+03 3.49E+00 NR 3.26E-03 5.58E+00 7.33E-02 2.03E-03 3.65E+00 7.63E-07 9.28E-03 2.74E-03 7.43E-02 NR 1.90E+02 1.55E-05 2.87E-01 NR NR NR 2.28E+00 3.64E-05 NR #DIV/0! 3.53E-04 3.44E-04 1.46E-07 1.76E-03 2.49E-03 2.43E-02 1.19E-01 NR NR NR 3.04E-02 2.31E-07 1.32E-02 2.04E-02 3.38E-05 8.05E-05 5.73E-05 NR 1.27E-03 1.21E-05 2.70E-05 NR 1.94E-02 1.26E-02
HLW Silver Mordenite Absorbent Non-Debris 9.46E-14 8.45E-11 1.05E-10 1.53E-10 1.31E-13 1.66E-19 2.79E-14 3.91E-10 5.27E-17 2.18E-07 6.13E-10 NR 0.00E+00 1.69E+03 2.57E-13 7.99E-03 1.56E-09 9.53E-19 1.31E-13 2.39E-14 1.88E-11 NR 2.06E-09 1.84E-17 7.51E-11 NR NR NR 2.72E-09 6.27E-17 NR #DIV/0! 8.61E-16 1.42E-15 3.64E-19 3.64E-11 7.29E-13 1.57E-10 2.09E-13 NR NR NR 2.06E-11 0.00E+00 2.62E-13 1.79E-11 7.50E-17 8.73E-16 1.86E-15 NR 3.13E-15 5.29E-17 3.11E-19 NR 1.44E-15 4.28E-14
SSW Total 1.02E-01 2.20E+01 2.83E-01 2.88E+01 3.73E-02 5.56E-05 2.42E-02 3.37E-01 7.79E-04 8.06E+04 7.46E+02 NR 3.26E-03 1.07E+05 1.31E-01 1.01E+03 3.12E+02 8.78E-07 1.14E-01 8.90E-03 8.52E-02 NR 4.66E+03 3.08E-05 5.88E-01 NR NR NR 1.18E+01 2.38E-04 NR #DIV/0! 3.85E-04 1.05E-03 7.88E-07 8.14E-03 1.13E-02 4.78E-01 2.04E-01 NR NR NR 3.63E-02 2.31E-07 7.97E-01 2.71E-02 5.06E-05 2.85E-04 1.49E-04 NR 1.38E-03 2.87E-05 4.64E-04 NR 1.55E-01 3.23E-02
BBI 5.91E+05 1.99E+03 8.20E+04
Check 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% N/A 100% 100% 100% 100% 100% 100% 100% 100% 100% N/A 100% 100% 100% N/A N/A N/A 100% 100% N/A #DIV/0! 100% 100% 100% 100% 100% 100% 100% N/A N/A N/A 100% 100% 100% 100% 100% 100% 100% N/A 100% 100% 100% N/A 100% 100%
SE
CT
ION
1S
EC
TIO
N 2
SE
CT
ION
3A
SE
CT
ION
4S
EC
TIO
N 5
A
RPP-ENV-58562 Rev.03 5/9/2016 - 11:21 AM 103 of 118RPP-ENV-58562 Rev.03 9/26/2016 - 12:49 PM 103 of 124
RPP-ENV-58562, Rev. 3
A-11/A-12
Table A-5. Run Case 9 Radionuclides.
SVF-4095, IDF PA Case 9 - Removal of LAWPS - Mass Balance, MMR-50052
WASTE STREAM 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
LAW Glass Subtotal (IDF) 1.19E+01 3.35E+03 4.01E+03 3.87E+02 1.62E+01 1.69E-01 9.20E+03 8.69E+03 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 9.21E-03 1.40E+01 2.01E+02 0.00E+00 0.00E+00 0.00E+00 1.42E-01 1.16E+01 2.97E+00 1.18E-01 9.30E-02 1.71E+01 2.35E+02 2.63E+00 5.01E+03 1.05E+03 6.03E+03 7.98E+03 1.20E+02 7.47E-02 3.05E+00 1.33E+01 2.94E+02 0.00E+00 4.47E+01 0.00E+00 4.03E+03 1.40E+02 1.35E+05 1.35E+05 0.00E+00 0.00E+00 2.60E+04
LAW Spent Melter Subtotal (IDF) 1.64E-02 4.65E+00 5.51E+00 4.62E-01 1.73E-02 2.16E-04 1.10E+01 1.04E+01 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.10E-05 1.92E-02 2.33E-01 0.00E+00 0.00E+00 0.00E+00 1.83E-04 1.48E-02 3.92E-03 1.57E-04 1.27E-04 2.31E-02 2.79E-01 3.48E-03 6.18E+00 1.29E+00 8.11E+00 9.42E+00 1.69E-01 9.09E-05 3.93E-03 1.90E-02 4.20E-01 0.00E+00 5.90E-02 0.00E+00 5.29E+00 1.69E-01 1.68E+02 1.68E+02 0.00E+00 0.00E+00 2.78E+01
ETF Solid Waste Form to IDF 7.94E-03 1.23E+01 8.54E+01 1.60E+00 5.92E-02 8.94E-06 5.94E-01 5.61E-01 2.25E+00 1.66E-05 4.44E-10 2.06E-07 8.28E-08 1.86E-04 5.85E-02 4.08E+00 3.69E-15 7.47E-11 3.11E-17 2.76E-07 1.70E-05 2.87E-03 1.20E-04 3.35E-05 7.05E-05 2.59E-04 2.75E-03 5.67E-03 1.15E-03 1.97E-02 8.47E-03 4.86E-01 3.03E-04 9.70E-06 5.38E-02 1.19E+00 3.83E+00 1.12E-01 8.56E-05 9.95E+00 2.79E+00 1.22E+02 1.22E+02 2.03E-07 5.65E-03 2.13E-01
Solid Waste Forms from Treatment Processes (IDF) 6.28E-05 7.65E-03 1.30E-02 1.31E-02 1.19E+01 5.37E-02 2.93E+03 2.77E+03 0.00E+00 2.66E-03 6.67E-07 3.99E-05 2.00E-05 3.50E-08 1.57E-06 7.63E-04 1.20E-09 3.93E-09 5.55E-09 2.28E-08 1.84E-06 5.10E-07 2.05E-08 1.55E-08 1.99E-06 7.73E-03 4.56E-07 1.38E-02 1.34E-02 7.64E-03 9.54E-04 2.78E-04 8.94E-09 7.60E-07 4.94E-04 8.41E-04 0.00E+00 4.03E-04 1.67E-05 3.62E-02 5.40E-03 2.58E+01 2.58E+01 2.70E-04 -1.02E-03 1.62E+01
Non-IDF Stream -2.12E-03 4.37E+02 3.03E+00 2.25E-01 5.99E-01 7.08E+02 3.86E+07 3.64E+07 5.89E+02 3.17E+06 7.96E+02 4.76E+04 2.39E+04 1.37E-05 -9.06E+00 -1.94E+02 1.43E+00 4.69E+00 6.62E+00 8.19E+00 6.36E+02 2.14E+02 8.76E+00 6.04E+00 9.06E+01 2.24E+03 1.95E+02 4.27E+04 9.03E+03 1.42E+05 7.10E+04 1.11E-01 6.79E-01 6.40E+01 8.72E-03 1.89E-01 2.80E+03 1.40E+03 3.68E+03 1.25E+05 6.46E-02 4.29E+07 4.29E+07 3.39E+03 2.87E+03 2.24E+01
BBI 1.20E+01 3.89E+03 4.13E+03 3.91E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 5.51E+02 3.57E+06 9.07E+02 5.30E+04 2.55E+04 9.95E-03 4.14E+00 6.77E+00 1.48E+00 5.16E+00 6.77E+00 8.87E+00 6.82E+02 2.37E+02 9.71E+00 6.50E+00 1.15E+02 2.63E+03 2.15E+02 4.94E+04 1.08E+04 1.57E+05 8.38E+04 1.22E+02 8.26E-01 7.23E+01 1.35E+01 2.98E+02 2.82E+03 1.62E+03 4.10E+03 1.44E+05 1.44E+02 4.76E+07 4.76E+07 3.73E+03 3.17E+03 2.65E+04
HTWOS Feed 1.20E+01 3.89E+03 4.13E+03 3.91E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 5.91E+02 3.57E+06 9.07E+02 5.30E+04 2.55E+04 9.95E-03 4.14E+00 6.77E+00 1.48E+00 5.16E+00 6.77E+00 8.87E+00 6.82E+02 2.37E+02 9.71E+00 6.50E+00 1.15E+02 2.64E+03 2.16E+02 5.14E+04 1.09E+04 1.57E+05 8.39E+04 1.22E+02 8.27E-01 7.23E+01 1.35E+01 2.98E+02 2.82E+03 1.62E+03 4.10E+03 1.44E+05 1.44E+02 4.76E+07 4.76E+07 3.73E+03 3.17E+03 2.65E+04
HTWOS Feed Adjusted Minus TF and TRU Accumulation 1.20E+01 3.83E+03 4.11E+03 3.90E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 5.91E+02 3.27E+06 8.25E+02 4.95E+04 2.45E+04 9.43E-03 4.55E+00 9.37E+00 1.43E+00 4.83E+00 6.63E+00 8.39E+00 6.51E+02 2.19E+02 8.95E+00 6.20E+00 1.08E+02 2.52E+03 1.99E+02 4.83E+04 1.02E+04 1.50E+05 8.00E+04 1.21E+02 7.63E-01 6.80E+01 1.34E+01 2.96E+02 2.81E+03 1.48E+03 3.80E+03 1.33E+05 1.44E+02 4.41E+07 4.41E+07 3.49E+03 2.96E+03 2.65E+04
ACCUMULATION STREAM 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
PT-Accumulation 1.08E-03 1.99E+01 6.60E-01 9.20E-02 5.57E-02 4.46E+00 4.05E+05 3.82E+05 1.23E-01 9.66E+04 2.81E+01 1.81E+03 5.96E+02 2.91E-06 -4.98E-01 -3.00E+00 3.31E-03 1.37E-01 9.55E-03 5.37E-02 3.30E+00 1.54E+00 6.30E-02 5.91E-02 6.74E-01 3.93E+01 1.37E+00 5.43E+02 1.25E+02 1.66E+03 9.32E+02 1.90E-02 9.24E-03 9.36E-01 3.38E-03 7.42E-02 3.26E+00 3.92E+01 1.12E+02 3.03E+03 4.64E-02 9.52E+05 9.52E+05 9.53E+01 8.66E+01 2.01E+01
TF-Accumulation 9.71E-06 6.66E+01 2.11E+01 1.97E+00 7.56E-02 2.39E-02 1.87E+04 1.77E+04 2.24E-01 3.00E+05 8.13E+01 3.51E+03 1.05E+03 5.21E-04 -4.03E-01 -2.60E+00 4.68E-02 3.26E-01 1.33E-01 4.78E-01 3.06E+01 1.77E+01 7.61E-01 3.00E-01 6.37E+00 1.21E+02 1.71E+01 3.16E+03 6.69E+02 6.60E+03 3.90E+03 9.33E-01 6.38E-02 4.30E+00 1.39E-01 2.52E+00 4.69E+00 1.37E+02 3.04E+02 1.17E+04 5.12E-02 3.55E+06 3.55E+06 2.45E+02 2.12E+02 8.95E+00
TRU-Accumulation 3.93E-14 5.50E-04 3.41E-06 6.30E-05 6.28E-06 1.86E-09 2.64E+00 2.50E+00 8.33E-04 1.13E+00 3.05E-05 1.77E-02 7.07E-03 7.63E-08 1.47E-06 4.74E-12 2.31E-10 4.67E-06 1.94E-12 6.29E-08 5.45E-09 7.26E-03 2.34E-04 7.01E-05 2.54E-05 2.82E-02 5.37E-03 2.23E+00 2.70E-01 3.27E-01 7.48E-01 5.56E-05 1.33E-05 3.19E-05 5.76E-07 1.22E-05 3.85E-03 1.44E-04 5.41E-04 1.94E-02 3.44E-05 3.34E+01 3.34E+01 1.89E-02 1.73E-02 1.18E-02
LAW Accumulation 2.47E-04 7.93E-01 1.36E-01 1.86E-02 5.63E-03 7.87E-06 7.63E-01 7.21E-01 1.52E-02 0.00E+00 0.00E+00 0.00E+00 0.00E+00 5.65E-07 3.51E-03 4.85E-02 0.00E+00 0.00E+00 0.00E+00 9.26E-06 5.63E-04 2.86E-04 1.17E-05 1.17E-05 5.53E-04 3.44E-02 2.52E-04 4.51E-01 1.04E-01 1.48E-01 7.98E-01 4.06E-03 7.72E-06 9.63E-05 7.46E-04 1.64E-02 7.40E-02 7.18E-03 0.00E+00 5.52E-01 9.17E-03 1.38E+01 1.38E+01 0.00E+00 0.00E+00 4.82E+00
HLW-Accumulation 2.17E-07 3.43E-01 4.12E-04 4.60E-05 9.76E-04 2.77E-02 2.96E+03 2.80E+03 2.52E-05 5.61E+03 1.66E+00 1.03E+02 3.31E+01 1.56E-09 -2.76E-02 -1.81E-01 1.74E-04 7.38E-03 5.17E-04 3.16E-03 1.96E-01 8.57E-02 3.52E-03 3.16E-03 3.89E-02 2.19E+00 7.67E-02 3.16E+01 7.28E+00 9.55E+01 5.29E+01 9.92E-06 5.32E-04 5.34E-02 1.78E-06 3.90E-05 1.84E+00 2.14E+00 6.23E+00 1.67E+02 2.25E-05 5.53E+04 5.53E+04 5.09E+00 4.45E+00 6.36E-04
SLAW-Accumulation 6.22E-04 1.41E+00 2.05E+00 3.56E-02 4.68E-01 1.19E-04 1.35E+01 1.28E+01 1.86E-02 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.16E-05 7.00E-03 1.30E+00 0.00E+00 0.00E+00 0.00E+00 1.85E-05 1.13E-03 5.69E-04 2.34E-05 2.19E-05 1.13E-03 6.24E-02 5.08E-04 8.25E-01 1.90E-01 4.13E-01 1.44E+00 7.65E-03 1.37E-05 2.55E-04 1.38E-03 3.03E-02 5.86E-01 1.41E-02 0.00E+00 1.10E+00 1.88E-01 4.11E+01 4.11E+01 0.00E+00 0.00E+00 3.54E+02
LAWPS-Accumulation 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00
ETF-Accumulation 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00
LERF-Accumulation 7.44E-06 1.51E-01 7.00E-02 3.37E-03 1.20E-04 1.70E-09 1.90E-04 1.80E-04 3.93E-03 4.55E-31 1.21E-35 6.63E-33 2.65E-33 3.05E-07 7.47E-04 3.18E-02 9.38E-41 1.91E-36 7.89E-43 9.74E-10 5.99E-08 2.78E-08 1.14E-09 1.02E-09 2.86E-08 2.20E-06 2.49E-08 2.94E-05 6.76E-06 2.35E-05 5.10E-05 7.15E-04 1.54E-06 1.41E-08 1.29E-04 2.83E-03 3.81E+00 1.03E-03 1.62E-30 8.06E-02 4.85E-03 1.56E+00 1.56E+00 7.12E-33 1.98E-28 3.65E-04
Total Accumulation 1.96E-03 8.92E+01 2.40E+01 2.12E+00 6.06E-01 4.51E+00 4.26E+05 4.02E+05 3.86E-01 4.02E+05 1.11E+02 5.42E+03 1.68E+03 5.36E-04 -9.18E-01 -4.40E+00 5.03E-02 4.71E-01 1.43E-01 5.35E-01 3.41E+01 1.93E+01 8.27E-01 3.62E-01 7.08E+00 1.63E+02 1.86E+01 3.74E+03 8.02E+02 8.36E+03 4.89E+03 9.64E-01 7.36E-02 5.29E+00 1.44E-01 2.64E+00 1.43E+01 1.78E+02 4.22E+02 1.49E+04 2.99E-01 4.56E+06 4.56E+06 3.46E+02 3.03E+02 3.88E+02
Accumulation minus TF and TRU 1.96E-03 2.25E+01 2.91E+00 1.50E-01 5.30E-01 4.49E+00 4.08E+05 3.85E+05 1.61E-01 1.02E+05 2.98E+01 1.91E+03 6.29E+02 1.54E-05 -5.14E-01 -1.80E+00 3.48E-03 1.44E-01 1.01E-02 5.69E-02 3.50E+00 1.63E+00 6.66E-02 6.23E-02 7.14E-01 4.16E+01 1.45E+00 5.76E+02 1.33E+02 1.76E+03 9.87E+02 3.14E-02 9.80E-03 9.89E-01 5.64E-03 1.24E-01 9.58E+00 4.14E+01 1.18E+02 3.20E+03 2.48E-01 1.01E+06 1.01E+06 1.00E+02 9.10E+01 3.79E+02
ADJUSTED INVENTORY TO INCLUDE ACCUMULATION-Radionuclides decayed to 1/1/2008 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
LAW Glass Subtotal (IDF) 1.19E+01 3.37E+03 4.02E+03 3.87E+02 1.65E+01 1.70E-01 9.30E+03 8.78E+03 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 9.22E-03 1.25E+01 1.62E+02 0.00E+00 0.00E+00 0.00E+00 1.43E-01 1.17E+01 2.99E+00 1.19E-01 9.39E-02 1.72E+01 2.39E+02 2.65E+00 5.07E+03 1.06E+03 6.10E+03 8.08E+03 1.20E+02 7.57E-02 3.09E+00 1.33E+01 2.94E+02 0.00E+00 4.59E+01 0.00E+00 4.13E+03 1.41E+02 1.38E+05 1.38E+05 0.00E+00 0.00E+00 2.64E+04
LAW Spent Melter Subtotal (IDF) 1.64E-02 4.67E+00 5.51E+00 4.63E-01 1.76E-02 2.17E-04 1.11E+01 1.05E+01 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.11E-05 1.70E-02 1.88E-01 0.00E+00 0.00E+00 0.00E+00 1.85E-04 1.48E-02 3.95E-03 1.58E-04 1.29E-04 2.33E-02 2.83E-01 3.50E-03 6.25E+00 1.31E+00 8.20E+00 9.54E+00 1.69E-01 9.21E-05 3.98E-03 1.90E-02 4.20E-01 0.00E+00 6.06E-02 0.00E+00 5.42E+00 1.70E-01 1.72E+02 1.72E+02 0.00E+00 0.00E+00 2.82E+01
ETF Solid Waste Form to IDF 7.94E-03 1.24E+01 8.54E+01 1.60E+00 6.03E-02 9.00E-06 6.01E-01 5.67E-01 2.25E+00 1.72E-05 4.60E-10 2.14E-07 8.50E-08 1.86E-04 5.19E-02 3.30E+00 3.70E-15 7.69E-11 3.12E-17 2.78E-07 1.71E-05 2.89E-03 1.21E-04 3.38E-05 7.10E-05 2.63E-04 2.77E-03 5.73E-03 1.17E-03 2.00E-02 8.58E-03 4.86E-01 3.07E-04 9.84E-06 5.38E-02 1.19E+00 3.84E+00 1.15E-01 8.82E-05 1.02E+01 2.79E+00 1.24E+02 1.24E+02 2.09E-07 5.82E-03 2.16E-01
Solid Waste Forms from Treatment Processes (IDF) 6.28E-05 7.69E-03 1.30E-02 1.31E-02 1.21E+01 5.41E-02 2.96E+03 2.80E+03 0.00E+00 2.74E-03 6.92E-07 4.15E-05 2.05E-05 3.50E-08 1.39E-06 6.17E-04 1.20E-09 4.05E-09 5.56E-09 2.30E-08 1.85E-06 5.14E-07 2.07E-08 1.56E-08 2.01E-06 7.86E-03 4.59E-07 1.40E-02 1.35E-02 7.73E-03 9.66E-04 2.78E-04 9.06E-09 7.71E-07 4.94E-04 8.42E-04 0.00E+00 4.14E-04 1.72E-05 3.71E-02 5.41E-03 2.64E+01 2.64E+01 2.77E-04 -1.05E-03 1.64E+01
Non-IDF Stream -2.12E-03 4.40E+02 3.03E+00 2.25E-01 6.09E-01 7.13E+02 3.90E+07 3.68E+07 5.89E+02 3.27E+06 8.24E+02 4.94E+04 2.45E+04 1.37E-05 -8.03E+00 -1.57E+02 1.43E+00 4.83E+00 6.63E+00 8.25E+00 6.40E+02 2.16E+02 8.83E+00 6.10E+00 9.12E+01 2.28E+03 1.96E+02 4.32E+04 9.15E+03 1.44E+05 7.19E+04 1.11E-01 6.87E-01 6.49E+01 8.72E-03 1.89E-01 2.81E+03 1.43E+03 3.80E+03 1.28E+05 6.47E-02 4.39E+07 4.39E+07 3.49E+03 2.96E+03 2.27E+01
1.20E+01 3.83E+03 4.11E+03 3.90E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 5.91E+02 3.27E+06 8.24E+02 4.94E+04 2.45E+04 9.43E-03 4.49E+00 9.02E+00 1.43E+00 4.83E+00 6.63E+00 8.39E+00 6.51E+02 2.19E+02 8.95E+00 6.20E+00 1.08E+02 2.52E+03 1.99E+02 4.82E+04 1.02E+04 1.50E+05 7.99E+04 1.21E+02 7.63E-01 6.80E+01 1.34E+01 2.96E+02 2.81E+03 1.48E+03 3.80E+03 1.33E+05 1.44E+02 4.40E+07 4.40E+07 3.49E+03 2.96E+03 2.65E+04
100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 101% 104% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100%
INVENTORY TO INCLUDE ACCUMULATION-Radionuclides decayed to 1/1/2051 IDF Waste Streams Only 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
LAW Glass Subtotal (IDF) 2.43E-12 4.07E+02 8.13E-02 3.87E+02 1.65E+01 9.14E-08 3.45E+03 3.26E+03 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 9.05E-03 3.17E+00 9.18E-01 0.00E+00 0.00E+00 0.00E+00 9.36E-02 1.17E+01 2.99E+00 1.19E-01 9.39E-02 1.72E+01 1.70E+02 2.65E+00 5.06E+03 1.05E+03 5.92E+03 1.02E+03 9.75E+01 7.57E-02 3.08E+00 4.78E+00 5.66E+01 0.00E+00 4.59E+01 0.00E+00 3.07E+03 1.41E+02 4.90E+04 4.90E+04 0.00E+00 0.00E+00 2.64E+04
LAW Spent Melter Subtotal (IDF) 3.35E-15 5.64E-01 1.12E-04 4.63E-01 1.76E-02 1.17E-10 4.14E+00 3.90E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.09E-05 4.33E-03 1.07E-03 0.00E+00 0.00E+00 0.00E+00 1.20E-04 1.48E-02 3.95E-03 1.58E-04 1.29E-04 2.33E-02 2.02E-01 3.50E-03 6.25E+00 1.30E+00 7.92E+00 1.20E+00 1.37E-01 9.21E-05 3.97E-03 6.82E-03 8.10E-02 0.00E+00 6.06E-02 0.00E+00 4.04E+00 1.70E-01 6.11E+01 6.11E+01 0.00E+00 0.00E+00 2.82E+01
ETF Solid Waste Form to IDF 1.62E-15 1.49E+00 1.73E-03 1.60E+00 6.03E-02 4.85E-12 2.23E-01 2.10E-01 2.24E+00 1.23E-05 5.09E-11 6.65E-09 1.60E-10 1.83E-04 1.32E-02 1.87E-02 3.69E-15 7.68E-11 3.12E-17 1.81E-07 1.71E-05 2.89E-03 1.21E-04 3.38E-05 7.10E-05 1.88E-04 2.77E-03 5.73E-03 1.16E-03 1.89E-02 1.08E-03 3.93E-01 3.07E-04 9.80E-06 1.93E-02 2.29E-01 3.42E-01 1.15E-01 3.09E-07 7.58E+00 2.79E+00 4.42E+01 4.42E+01 2.09E-07 9.15E-04 2.16E-01
Solid Waste Forms from Treatment Processes (IDF) 1.28E-17 9.29E-04 2.63E-07 1.31E-02 1.21E+01 2.91E-08 1.10E+03 1.04E+03 0.00E+00 1.97E-03 7.65E-08 1.29E-06 3.87E-08 3.44E-08 3.57E-07 3.50E-06 1.19E-09 4.05E-09 5.56E-09 1.50E-08 1.85E-06 5.14E-07 2.07E-08 1.56E-08 2.01E-06 5.59E-03 4.59E-07 1.40E-02 1.35E-02 7.24E-03 1.22E-04 2.25E-04 9.06E-09 7.68E-07 1.77E-04 1.62E-04 0.00E+00 4.14E-04 6.02E-08 2.76E-02 5.41E-03 9.37E+00 9.37E+00 2.77E-04 6.90E-05 1.64E+01
SSW FRACTIONS BASED ON 10-010 and 10-009 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
HEPA fraction NR NR NR 51.81% 1.03% 52.45% 50.81% NR 10.40% NR 65.24% 64.99% 65.27% NR NR NR NR NR NR NR 68.98% 68.94% 68.90% 68.85% 54.86% 68.68% 68.39% 68.53% 68.48% 70.74% 68.04% NR NR NR NR NR 0.01% 56.98% 62.75% 57.75% 71.82% 65.75% NR NR NR 87.60%
IX Resin fraction NR NR NR 43.80% 0.14% 8.96% 9.27% NR 1.53% NR 7.64% 7.67% 7.61% NR NR NR NR NR NR NR 0.00% 0.00% 0.00% 0.00% 42.37% 0.00% 0.00% 0.00% 0.00% 3.83% 0.00% NR NR NR NR NR 49.09% 20.28% 19.08% 19.89% 26.01% 0.09% NR NR NR 11.86%
LAW and HLW Carbon Bed fraction NR NR NR 0.00% 36.47% 0.00% 0.00% NR 34.07% NR 0.00% 0.00% 0.00% NR NR NR NR NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR NR NR 36.25% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00%
Other Debris fraction NR NR NR 4.39% 0.01% 38.59% 39.92% NR 24.63% NR 27.13% 27.34% 27.12% NR NR NR NR NR NR NR 31.02% 31.06% 31.10% 31.15% 2.77% 31.32% 31.61% 31.47% 31.52% 25.43% 31.96% NR NR NR NR NR 14.62% 22.75% 18.17% 22.35% 2.17% 34.16% NR NR NR 0.54%
HLW Silver Mordenite Absorbent fraction NR NR NR 0.00% 62.35% 0.00% 0.00% NR 29.36% NR 0.00% 0.00% 0.00% NR NR NR NR NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR NR NR 0.03% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00%
WTP SSW INVENTORY-Radionuclides decayed to 1/1/2008 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
HEPA Filters Debris NR NR NR 6.80E-03 1.25E-01 2.84E-02 1.51E+03 NR 0.00E+00 NR 4.51E-07 2.70E-05 1.34E-05 NR NR NR NR NR NR NR 1.27E-06 3.54E-07 1.43E-08 1.08E-08 1.10E-06 5.40E-03 3.14E-07 9.57E-03 9.27E-03 5.47E-03 6.57E-04 NR NR NR NR NR 0.00E+00 2.36E-04 1.08E-05 2.14E-02 3.89E-03 1.74E+01 NR NR NR 1.44E+01
IX Resin Non-Debris NR NR NR 5.74E-03 1.66E-02 4.84E-03 2.75E+02 NR 0.00E+00 NR 5.28E-08 3.18E-06 1.56E-06 NR NR NR NR NR NR NR 6.19E-13 1.77E-13 6.06E-15 7.33E-15 8.51E-07 5.69E-08 1.61E-13 1.02E-07 9.89E-08 2.96E-04 7.15E-09 NR NR NR NR NR 0.00E+00 8.39E-05 3.28E-06 7.38E-03 1.41E-03 2.48E-02 NR NR NR 1.95E+00
LAW and HLW Carbon Beds Non-Debris NR NR NR 1.36E-13 4.42E+00 1.01E-11 4.67E-07 NR 0.00E+00 NR 1.43E-18 8.93E-17 4.37E-17 NR NR NR NR NR NR NR 6.91E-19 2.13E-19 8.83E-21 8.32E-21 2.02E-17 3.02E-15 1.93E-19 5.42E-15 5.23E-15 1.03E-14 3.79E-16 NR NR NR NR NR 0.00E+00 1.72E-14 1.11E-16 1.54E-12 3.94E-13 3.06E-09 NR NR NR 2.17E-09
Other Debris Debris NR NR NR 5.75E-04 1.09E-03 2.09E-02 1.18E+03 NR 0.00E+00 NR 1.88E-07 1.13E-05 5.57E-06 NR NR NR NR NR NR NR 5.73E-07 1.60E-07 6.43E-09 4.87E-09 5.56E-08 2.46E-03 1.45E-07 4.40E-03 4.27E-03 1.97E-03 3.09E-04 NR NR NR NR NR 0.00E+00 9.41E-05 3.12E-06 8.29E-03 1.17E-04 9.02E+00 NR NR NR 8.85E-02
HLW Silver Mordenite Absorbent Non-Debris NR NR NR 1.31E-16 7.56E+00 2.00E-11 9.27E-07 NR 0.00E+00 NR 3.59E-19 2.74E-17 1.32E-17 NR NR NR NR NR NR NR 1.38E-18 4.25E-19 1.77E-20 1.66E-20 1.31E-20 6.05E-15 3.85E-19 1.08E-14 1.05E-14 6.06E-15 7.58E-16 NR NR NR NR NR 0.00E+00 2.77E-14 2.38E-17 2.48E-12 4.83E-14 6.12E-09 NR NR NR 1.83E-12
SSW Total NR NR NR 1.31E-02 1.21E+01 5.41E-02 2.96E+03 NR 0.00E+00 NR 6.92E-07 4.15E-05 2.05E-05 NR NR NR NR NR NR NR 1.85E-06 5.14E-07 2.07E-08 1.56E-08 2.01E-06 7.86E-03 4.59E-07 1.40E-02 1.35E-02 7.73E-03 9.66E-04 NR NR NR NR NR 0.00E+00 4.14E-04 1.72E-05 3.71E-02 5.41E-03 2.64E+01 NR NR NR 1.64E+01
BBI 2.94E+01 3.90E+07 4.76E+07 2.65E+04
Check N/A N/A N/A 100% 100% 100% 100% N/A #DIV/0! N/A 100% 100% 100% N/A N/A N/A N/A N/A N/A N/A 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% N/A N/A N/A N/A N/A #DIV/0! 100% 100% 100% 100% 100% N/A N/A N/A 100%
WTP SSW INVENTORY-Radionuclides decayed to 1/1/2051 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
HEPA Filters Debris NR NR NR 6.80E-03 1.25E-01 1.53E-08 5.59E+02 NR 0.00E+00 NR 4.99E-08 8.40E-07 2.52E-08 NR NR NR NR NR NR NR 1.27E-06 3.54E-07 1.43E-08 1.08E-08 1.10E-06 3.84E-03 3.14E-07 9.56E-03 9.23E-03 5.12E-03 8.30E-05 NR NR NR NR NR 0.00E+00 2.36E-04 3.78E-08 1.59E-02 3.89E-03 6.16E+00 NR NR NR 1.44E+01
IX Resin Non-Debris NR NR NR 5.74E-03 1.66E-02 2.61E-09 1.02E+02 NR 0.00E+00 NR 5.84E-09 9.91E-08 2.94E-09 NR NR NR NR NR NR NR 6.19E-13 1.77E-13 6.06E-15 7.33E-15 8.51E-07 4.05E-08 1.61E-13 1.02E-07 9.84E-08 2.76E-04 9.03E-10 NR NR NR NR NR 0.00E+00 8.39E-05 1.15E-08 5.49E-03 1.41E-03 8.79E-03 NR NR NR 1.95E+00
LAW and HLW Carbon Beds Non-Debris NR NR NR 1.36E-13 4.42E+00 5.43E-18 1.73E-07 NR 0.00E+00 NR 1.58E-19 2.78E-18 8.23E-20 NR NR NR NR NR NR NR 6.90E-19 2.13E-19 8.83E-21 8.32E-21 2.02E-17 2.15E-15 1.93E-19 5.41E-15 5.21E-15 9.61E-15 4.78E-17 NR NR NR NR NR 0.00E+00 1.72E-14 3.89E-19 1.15E-12 3.94E-13 1.09E-09 NR NR NR 2.17E-09
Other Debris Debris NR NR NR 5.75E-04 1.09E-03 1.12E-08 4.39E+02 NR 0.00E+00 NR 2.08E-08 3.53E-07 1.05E-08 NR NR NR NR NR NR NR 5.72E-07 1.60E-07 6.43E-09 4.87E-09 5.56E-08 1.75E-03 1.45E-07 4.39E-03 4.25E-03 1.84E-03 3.90E-05 NR NR NR NR NR 0.00E+00 9.41E-05 1.09E-08 6.17E-03 1.17E-04 3.20E+00 NR NR NR 8.85E-02
HLW Silver Mordenite Absorbent Non-Debris NR NR NR 1.31E-16 7.56E+00 1.08E-17 3.44E-07 NR 0.00E+00 NR 3.98E-20 8.55E-19 2.48E-20 NR NR NR NR NR NR NR 1.38E-18 4.25E-19 1.77E-20 1.66E-20 1.31E-20 4.30E-15 3.85E-19 1.08E-14 1.04E-14 5.68E-15 9.56E-17 NR NR NR NR NR 0.00E+00 2.77E-14 8.32E-20 1.85E-12 4.83E-14 2.17E-09 NR NR NR 1.83E-12SE
CT
ION
5B
SE
CT
ION
1S
EC
TIO
N 2
SE
CT
ION
3A
SE
CT
ION
4S
EC
TIO
N 5
AS
EC
TIO
N 3
B
RPP-ENV-58562 Rev.03 5/9/2016 - 11:21 AM 104 of 118RPP-ENV-58562 Rev.03 9/26/2016 - 12:49 PM 104 of 124
RPP-ENV-58562, Rev. 3
A-13/A-14
Table A-6. Run Case 9 Chemicals.
SVF-4095, IDF PA Case 9 - Removal of LAWPS - Mass Balance, MMR-50052
WASTE STREAM Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
LAW Glass Subtotal (IDF) 9.77E+02 2.30E+07 4.68E+03 2.17E+07 6.78E+00 4.96E+02 6.60E+04 5.65E+03 5.40E+04 7.35E+05 4.92E+05 4.93E-01 3.57E+02 1.11E+06 2.76E+07 0.00E+00 9.37E+05 0.00E+00 7.44E+06 6.38E+06 0.00E+00 6.49E+03 7.87E+07 3.08E+03 1.96E+03 0.00E+00 0.00E+00 0.00E+00 7.02E+04 2.12E+03 0.00E+00 0.00E+00 8.53E+01 2.73E+02 0.00E+00 3.06E+03 3.49E+03 5.03E+03 1.57E+08 0.00E+00 3.14E+06 0.00E+00 4.65E+01 5.94E-02 1.54E+03 1.84E+03 0.00E+00 8.55E+06 0.00E+00 0.00E+00 7.88E+03 6.67E-01 4.13E+03 8.09E+01 1.69E+07 1.58E+07
LAW Spent Melter Subtotal (IDF) 1.39E+00 2.77E+04 5.58E+00 2.61E+04 1.51E-02 6.33E-01 8.70E+01 7.22E+00 7.52E+01 8.23E+02 6.58E+02 6.00E-04 4.49E-01 1.27E+03 3.31E+04 0.00E+00 1.08E+03 0.00E+00 5.81E+03 7.65E+03 0.00E+00 7.76E+00 1.05E+05 4.20E+00 2.58E+00 0.00E+00 0.00E+00 0.00E+00 8.32E+01 3.33E+00 0.00E+00 0.00E+00 1.05E-01 3.34E-01 0.00E+00 5.42E+00 4.20E+00 6.13E+00 1.84E+05 0.00E+00 3.64E+03 0.00E+00 5.63E-02 9.92E-05 1.64E+00 2.07E+00 0.00E+00 1.02E+04 0.00E+00 0.00E+00 1.04E+01 9.41E-04 7.07E+00 1.07E-01 2.03E+04 1.89E+04
ETF Solid Waste Form to IDF 2.61E+00 1.84E+01 9.08E+01 5.95E+01 9.99E-01 2.14E+00 2.97E+02 4.83E-01 1.05E+03 8.67E+02 3.89E+00 3.21E-05 3.37E+00 4.76E+03 2.85E+02 8.98E+02 7.05E+00 2.73E-03 7.95E+00 1.14E+00 3.38E+01 2.98E+01 3.48E+05 1.01E+01 5.57E+00 4.64E+01 1.64E+05 1.23E+05 8.62E+03 7.96E+00 2.38E+02 0.00E+00 1.72E-04 1.19E+00 0.00E+00 1.17E+01 6.84E+01 9.85E+01 1.84E+03 0.00E+00 0.00E+00 1.78E+03 1.22E+01 6.32E-04 1.26E-02 5.67E+01 2.83E-13 1.07E-05 1.45E-05 7.83E+03 8.25E+00 2.47E-05 4.58E-03 2.29E-03 2.29E+01 1.42E-05
Solid Waste Forms from Treatment Processes (IDF) 7.37E-02 2.18E+01 2.26E-01 2.88E+01 2.82E-02 5.56E-05 2.50E-02 3.57E-01 8.31E-04 8.00E+04 7.43E+02 1.56E-01 3.23E-03 1.05E+05 1.30E-01 1.03E+03 3.11E+02 8.71E-07 1.14E-01 8.72E-03 8.37E-02 1.41E-02 4.57E+03 2.97E-05 4.33E-01 0.00E+00 0.00E+00 0.00E+00 1.18E+01 2.38E-04 4.00E+03 6.81E-07 2.81E-04 1.05E-03 7.48E-07 8.14E-03 1.13E-02 4.00E-01 2.01E-01 6.04E+03 0.00E+00 0.00E+00 3.55E-02 2.02E-07 9.56E-01 3.03E-02 5.05E-05 2.85E-04 1.46E-04 0.00E+00 1.37E-03 2.81E-05 4.63E-04 2.46E-06 1.55E-01 3.19E-02
Non-IDF Stream 2.74E+03 2.51E+06 9.04E+01 1.52E+06 8.48E+03 2.84E+00 4.80E+05 2.98E+03 6.54E+03 4.97E+03 6.71E+04 2.06E+03 2.34E+03 3.54E+04 1.62E+06 1.35E+01 1.73E+04 4.20E+04 7.81E+05 2.25E+04 4.59E+05 2.49E+01 2.28E+06 5.98E+03 1.16E+05 1.67E+07 5.99E+07 2.54E+07 2.71E+03 1.22E+00 5.13E+06 8.12E+02 7.28E+02 1.70E-01 8.92E+02 1.41E+00 1.60E+02 3.47E+01 5.92E+06 -6.04E+03 -3.14E+06 3.81E+06 6.07E+04 2.32E+02 1.32E+00 1.01E+03 6.02E+04 1.38E+03 6.67E+03 8.62E+05 5.84E+05 2.37E+03 2.01E+01 4.63E+02 4.32E+02 4.01E+05
BBI 4.03E+03 8.67E+06 4.88E+03 1.52E+04 9.42E+03 5.02E+02 5.61E+05 8.87E+03 6.96E+03 8.27E+05 5.91E+05 2.09E+03 2.91E+03 1.28E+06 1.27E+06 1.99E+03 9.57E+05 3.20E+04 1.94E+03 2.19E+04 1.64E+05 6.56E+03 4.92E+07 9.70E+03 9.87E+04 1.19E+07 5.60E+07 4.45E+06 8.20E+04 2.14E+03 5.18E+06 8.43E+02 8.45E+02 2.78E+02 9.47E+02 3.09E+03 3.73E+03 5.18E+03 8.41E+05 0.00E+00 0.00E+00 3.82E+06 4.23E+04 2.72E+02 1.56E+03 2.92E+03 6.15E+04 1.51E+03 6.98E+03 8.71E+05 6.45E+05 2.58E+03 4.16E+03 5.81E+02 6.08E+03 4.09E+05
HTWOS Feed 4.03E+03 2.61E+07 4.88E+03 2.33E+07 9.42E+03 5.02E+02 6.02E+05 8.87E+03 6.24E+04 8.27E+05 5.91E+05 2.09E+03 2.91E+03 1.28E+06 2.94E+07 1.99E+03 9.57E+05 4.47E+04 8.23E+06 6.41E+06 4.77E+05 6.56E+03 8.17E+07 9.70E+03 1.25E+05 1.68E+07 6.02E+07 2.55E+07 8.20E+04 2.14E+03 5.20E+06 8.43E+02 8.77E+02 2.78E+02 9.47E+02 3.09E+03 3.73E+03 5.18E+03 1.63E+08 0.00E+00 0.00E+00 3.83E+06 6.40E+04 2.72E+02 1.56E+03 2.92E+03 6.15E+04 8.56E+06 6.98E+03 8.71E+05 6.47E+05 2.58E+03 4.16E+03 5.81E+02 1.69E+07 1.62E+07
HTWOS Feed Adjusted Minus TF and TRU Accumulation 3.82E+03 2.56E+07 4.87E+03 2.33E+07 8.70E+03 5.02E+02 5.46E+05 8.67E+03 6.20E+04 8.27E+05 5.63E+05 2.09E+03 2.73E+03 1.28E+06 2.93E+07 1.97E+03 9.56E+05 4.22E+04 8.23E+06 6.41E+06 4.65E+05 6.55E+03 8.16E+07 9.25E+03 1.20E+05 1.67E+07 6.01E+07 2.55E+07 8.16E+04 2.13E+03 5.14E+06 8.23E+02 8.23E+02 2.75E+02 9.39E+02 3.08E+03 3.72E+03 5.18E+03 1.63E+08 0.00E+00 0.00E+00 3.82E+06 6.11E+04 2.65E+02 1.56E+03 2.91E+03 6.03E+04 8.56E+06 6.79E+03 8.70E+05 5.96E+05 2.40E+03 4.15E+03 5.70E+02 1.69E+07 1.62E+07
ACCUMULATION STREAM Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
PT-Accumulation 9.76E+01 2.74E+04 1.68E+00 5.19E+00 2.00E+02 2.14E-01 2.36E+01 3.10E+01 2.27E+02 4.69E+02 1.74E+03 2.20E+01 2.40E+01 1.21E+03 1.47E+04 3.15E+00 3.06E+02 1.68E+02 4.08E-01 6.07E+02 6.13E+03 1.52E+00 3.59E+04 1.66E+02 1.71E+03 4.10E+03 4.10E+04 7.43E+03 1.84E+01 3.98E-01 1.36E+03 1.03E+01 9.32E+00 3.76E-02 4.53E+01 2.00E-01 1.10E+00 1.89E+00 8.31E+03 0.00E+00 0.00E+00 1.07E+03 2.97E+02 3.21E+01 1.18E+00 2.52E-01 8.69E+01 1.36E+01 1.19E+02 3.86E+02 4.10E+03 2.66E+01 1.16E-01 2.47E+01 9.65E-01 6.01E+03
TF-Accumulation 2.06E+02 4.62E+05 4.23E+00 2.53E+01 7.21E+02 3.32E-01 5.49E+04 1.99E+02 4.13E+02 6.64E+02 2.75E+04 1.04E+00 1.86E+02 6.18E+03 1.11E+05 1.88E+01 4.68E+02 2.50E+03 2.69E+00 1.68E+03 1.22E+04 3.50E+00 9.35E+04 4.52E+02 5.74E+03 7.10E+03 4.55E+04 6.24E+03 4.19E+02 7.34E+00 6.55E+04 2.02E+01 5.39E+01 3.49E+00 8.08E+00 5.07E+00 2.75E+00 2.71E+00 6.91E+04 0.00E+00 0.00E+00 2.68E+03 2.95E+03 6.09E+00 5.28E-01 2.99E+00 1.21E+03 1.15E+02 1.84E+02 7.76E+02 5.13E+04 1.78E+02 2.71E+00 1.11E+01 1.93E+01 1.92E+03
TRU-Accumulation 1.94E-02 2.91E+02 1.35E-02 2.92E-01 1.55E-01 6.08E-03 3.38E+02 9.73E-02 3.47E+00 1.25E+01 1.62E+01 1.47E-04 9.11E-01 1.57E+02 1.61E+02 2.34E-03 1.66E+00 1.96E-02 7.92E-115 2.52E+00 1.11E+00 3.96E-114 1.31E+03 7.92E-114 2.02E-01 3.37E+02 1.08E+03 1.08E-01 9.32E-01 0.00E+00 1.34E+03 0.00E+00 3.72E-02 0.00E+00 0.00E+00 1.13E-20 7.22E-01 8.75E-03 1.17E+02 0.00E+00 0.00E+00 7.15E+01 1.80E+00 0.00E+00 6.93E-04 0.00E+00 1.77E-08 1.73E-01 8.36E-113 5.54E+00 1.61E+01 2.50E-62 3.60E-299 6.08E-08 2.55E+00 1.21E+00
LAW Accumulation 1.75E-01 1.24E+03 3.41E-01 8.41E+02 3.69E-04 4.68E-02 4.82E+00 1.30E+00 1.70E+01 9.85E+01 9.66E+01 3.52E-05 4.12E-02 2.67E+02 1.07E+03 4.40E-01 4.32E+01 0.00E+00 8.58E-02 2.47E+02 0.00E+00 3.24E-01 7.60E+03 3.90E-01 2.99E-01 5.08E+02 2.06E+03 1.89E+03 2.08E+00 8.86E-02 1.79E+02 0.00E+00 7.73E-03 8.34E-03 0.00E+00 4.42E-02 2.27E-01 3.88E-01 5.68E+03 3.50E-04 5.93E+01 1.36E+02 4.27E-03 1.54E-05 2.84E-01 5.23E-02 0.00E+00 3.31E+02 0.00E+00 4.99E+01 7.57E-01 9.02E-05 2.56E-02 1.21E-02 6.55E+02 6.11E+02
HLW-Accumulation 5.37E+00 1.30E+03 1.02E-03 1.08E+03 1.19E+01 1.12E-04 7.01E-02 5.74E-01 6.17E+00 2.16E-02 4.19E+01 1.62E-01 1.35E+00 7.02E-02 8.49E+02 3.42E-03 8.42E-01 9.52E+00 3.26E+02 3.59E+01 3.54E+02 8.08E-04 1.05E+03 8.73E+00 9.71E+01 2.41E+00 8.70E+01 1.78E+01 1.04E-01 2.29E-04 9.35E-02 5.61E-01 5.41E-01 2.16E-05 2.39E+00 9.39E-05 7.02E-04 9.26E-04 2.96E+03 0.00E+00 2.94E-02 7.79E-02 1.73E+01 1.69E+00 3.75E-05 1.59E-04 4.70E+00 7.40E-01 5.34E+00 1.63E-01 2.30E+02 1.52E+00 6.44E-05 1.31E+00 5.10E-04 3.04E+02
SLAW-Accumulation 4.56E-01 1.53E+03 5.75E+00 9.23E+02 1.20E-03 8.68E-02 1.46E+01 2.30E+00 2.37E+01 4.55E+03 5.69E+02 4.50E-04 2.79E-01 1.80E+04 1.18E+03 2.93E+01 2.11E+02 0.00E+00 1.63E-01 2.71E+02 0.00E+00 8.14E-01 3.91E+04 7.48E-01 5.98E-01 7.22E+02 1.12E+04 2.96E+03 3.71E+00 1.70E-01 6.27E+02 0.00E+00 1.41E-02 2.09E-02 0.00E+00 8.13E-02 3.74E+00 6.47E+00 6.23E+03 6.09E-03 6.54E+01 1.03E+04 1.30E-02 3.25E-05 2.09E+01 1.07E+00 0.00E+00 3.62E+02 0.00E+00 6.11E+01 1.52E+00 2.53E-04 4.80E-02 2.33E-02 7.18E+02 6.70E+02
LAWPS-Accumulation 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00
ETF-Accumulation 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00
LERF-Accumulation 2.46E-02 3.58E-03 1.73E-01 1.91E-01 9.57E-03 7.99E-03 1.14E+00 6.83E-03 7.08E+00 1.61E+00 2.50E-02 1.04E-08 1.28E-02 1.62E+01 1.79E+00 1.65E+00 7.87E-03 1.37E-30 1.53E-02 7.85E-27 2.02E-26 6.28E-02 1.21E+03 7.35E-02 4.61E-02 1.48E-03 3.96E+02 9.65E+02 1.05E+01 1.63E-02 2.96E-02 0.00E+00 8.91E-07 1.67E-03 0.00E+00 7.76E-03 1.18E-01 1.92E-01 4.42E+00 0.00E+00 0.00E+00 1.09E+00 1.10E-01 6.44E-06 2.15E-05 3.19E-02 7.17E-39 6.62E-32 1.04E-34 3.06E+01 7.48E-05 2.47E-05 4.58E-03 2.29E-03 3.44E-02 4.63E-31
Total Accumulation 3.10E+02 4.94E+05 1.22E+01 2.88E+03 9.34E+02 6.94E-01 5.53E+04 2.34E+02 6.97E+02 5.80E+03 3.00E+04 2.32E+01 2.12E+02 2.58E+04 1.29E+05 5.33E+01 1.03E+03 2.67E+03 3.29E+02 2.84E+03 1.86E+04 6.22E+00 1.80E+05 6.27E+02 7.55E+03 1.28E+04 1.01E+05 1.95E+04 4.55E+02 8.01E+00 6.91E+04 3.10E+01 6.38E+01 3.56E+00 5.58E+01 5.41E+00 8.66E+00 1.17E+01 9.24E+04 6.44E-03 1.25E+02 1.43E+04 3.26E+03 3.98E+01 2.29E+01 4.40E+00 1.30E+03 8.22E+02 3.08E+02 1.31E+03 5.57E+04 2.07E+02 2.90E+00 3.71E+01 1.40E+03 9.52E+03
Accumulation minus TF and TRU 1.04E+02 3.14E+04 7.95E+00 2.85E+03 2.12E+02 3.56E-01 4.42E+01 3.52E+01 2.81E+02 5.12E+03 2.45E+03 2.22E+01 2.57E+01 1.95E+04 1.78E+04 3.45E+01 5.61E+02 1.78E+02 3.27E+02 1.16E+03 6.49E+03 2.72E+00 8.48E+04 1.76E+02 1.81E+03 5.33E+03 5.48E+04 1.33E+04 3.47E+01 6.74E-01 2.17E+03 1.09E+01 9.88E+00 6.85E-02 4.77E+01 3.33E-01 5.19E+00 8.94E+00 2.32E+04 6.44E-03 1.25E+02 1.15E+04 3.15E+02 3.38E+01 2.23E+01 1.40E+00 9.16E+01 7.07E+02 1.24E+02 5.28E+02 4.34E+03 2.82E+01 1.94E-01 2.60E+01 1.37E+03 7.59E+03
ADJUSTED INVENTORY TO INCLUDE ACCUMULATION Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
LAW Glass Subtotal (IDF) 1.00E+03 2.31E+07 4.69E+03 2.17E+07 6.95E+00 4.96E+02 6.61E+04 5.67E+03 5.43E+04 7.39E+05 4.95E+05 4.98E-01 3.61E+02 1.13E+06 2.76E+07 0.00E+00 9.38E+05 0.00E+00 7.44E+06 6.38E+06 0.00E+00 6.49E+03 7.88E+07 3.14E+03 1.99E+03 0.00E+00 0.00E+00 0.00E+00 7.02E+04 2.12E+03 0.00E+00 0.00E+00 8.64E+01 2.73E+02 0.00E+00 3.06E+03 3.49E+03 5.04E+03 1.57E+08 #DIV/0! #DIV/0! 0.00E+00 4.68E+01 6.69E-02 1.56E+03 1.85E+03 0.00E+00 8.55E+06 0.00E+00 0.00E+00 7.94E+03 6.75E-01 4.13E+03 8.46E+01 1.69E+07 1.58E+07
LAW Spent Melter Subtotal (IDF) 1.43E+00 2.77E+04 5.59E+00 2.61E+04 1.55E-02 6.33E-01 8.71E+01 7.25E+00 7.55E+01 8.28E+02 6.61E+02 6.07E-04 4.53E-01 1.29E+03 3.31E+04 0.00E+00 1.08E+03 0.00E+00 5.81E+03 7.65E+03 0.00E+00 7.77E+00 1.05E+05 4.28E+00 2.62E+00 0.00E+00 0.00E+00 0.00E+00 8.32E+01 3.33E+00 0.00E+00 0.00E+00 1.07E-01 3.34E-01 0.00E+00 5.42E+00 4.20E+00 6.14E+00 1.84E+05 #DIV/0! #DIV/0! 0.00E+00 5.65E-02 1.12E-04 1.66E+00 2.07E+00 0.00E+00 1.02E+04 0.00E+00 0.00E+00 1.05E+01 9.52E-04 7.07E+00 1.12E-01 2.03E+04 1.89E+04
ETF Solid Waste Form to IDF 2.68E+00 1.84E+01 9.10E+01 5.95E+01 1.02E+00 2.14E+00 2.97E+02 4.85E-01 1.06E+03 8.73E+02 3.90E+00 3.24E-05 3.41E+00 4.83E+03 2.85E+02 9.14E+02 7.05E+00 2.75E-03 7.95E+00 1.14E+00 3.43E+01 2.98E+01 3.48E+05 1.03E+01 5.66E+00 4.64E+01 1.64E+05 1.23E+05 8.62E+03 7.96E+00 2.38E+02 0.00E+00 1.74E-04 1.19E+00 0.00E+00 1.17E+01 6.85E+01 9.87E+01 1.84E+03 #DIV/0! #DIV/0! 1.78E+03 1.23E+01 7.12E-04 1.27E-02 5.67E+01 2.83E-13 1.07E-05 1.47E-05 7.84E+03 8.31E+00 2.50E-05 4.58E-03 2.39E-03 2.30E+01 1.42E-05
Solid Waste Forms from Treatment Processes (IDF) 7.57E-02 2.18E+01 2.26E-01 2.88E+01 2.89E-02 5.56E-05 2.50E-02 3.58E-01 8.35E-04 8.05E+04 7.46E+02 1.58E-01 3.26E-03 1.06E+05 1.30E-01 1.05E+03 3.11E+02 8.75E-07 1.14E-01 8.72E-03 8.48E-02 1.41E-02 4.58E+03 3.02E-05 4.40E-01 0.00E+00 0.00E+00 0.00E+00 1.18E+01 2.38E-04 4.00E+03 6.90E-07 2.85E-04 1.05E-03 7.86E-07 8.14E-03 1.13E-02 4.01E-01 2.01E-01 #DIV/0! #DIV/0! 0.00E+00 3.57E-02 2.27E-07 9.70E-01 3.03E-02 5.06E-05 2.85E-04 1.49E-04 0.00E+00 1.38E-03 2.84E-05 4.63E-04 2.58E-06 1.55E-01 3.19E-02
Non-IDF Stream 2.81E+03 2.52E+06 9.06E+01 1.52E+06 8.68E+03 2.84E+00 4.80E+05 2.99E+03 6.56E+03 5.00E+03 6.74E+04 2.09E+03 2.36E+03 3.60E+04 1.62E+06 1.37E+01 1.73E+04 4.22E+04 7.81E+05 2.25E+04 4.65E+05 2.49E+01 2.29E+06 6.10E+03 1.18E+05 1.67E+07 6.00E+07 2.54E+07 2.71E+03 1.22E+00 5.13E+06 8.23E+02 7.37E+02 1.70E-01 9.37E+02 1.41E+00 1.60E+02 3.48E+01 5.92E+06 #DIV/0! #DIV/0! 3.82E+06 6.10E+04 2.61E+02 1.34E+00 1.01E+03 6.03E+04 1.38E+03 6.79E+03 8.62E+05 5.88E+05 2.40E+03 2.01E+01 4.84E+02 4.32E+02 4.01E+05
3.82E+03 2.56E+07 4.87E+03 2.33E+07 8.69E+03 5.02E+02 5.46E+05 8.67E+03 6.20E+04 8.27E+05 5.63E+05 2.09E+03 2.73E+03 1.28E+06 2.93E+07 1.97E+03 9.56E+05 4.22E+04 8.23E+06 6.41E+06 4.65E+05 6.55E+03 8.16E+07 9.25E+03 1.20E+05 1.67E+07 6.01E+07 2.55E+07 8.16E+04 2.13E+03 5.14E+06 8.23E+02 8.23E+02 2.75E+02 9.37E+02 3.08E+03 3.72E+03 5.18E+03 1.63E+08 #DIV/0! #DIV/0! 3.82E+06 6.11E+04 2.61E+02 1.56E+03 2.91E+03 6.03E+04 8.56E+06 6.79E+03 8.70E+05 5.96E+05 2.40E+03 4.15E+03 5.68E+02 1.69E+07 1.62E+07
100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% #DIV/0! #DIV/0! 100% 100% 102% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100%
SSW FRACTIONS BASED ON 10-010 and 10-009 Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
HEPA fraction 4.53% 17.39% 17.89% 62.10% 6.43% 0.15% 5.17% 50.79% 0.21% 0.00% 94.18% NR 0.00% 0.00% 44.22% 0.00% 56.46% 7.86% 91.84% 69.10% 12.79% NR 40.68% 4.20% 13.13% NR NR NR 61.05% 1.03% 0.00% #DIV/0! 8.09% 5.61% 5.04% 78.35% 5.42% 31.35% 41.49% NR NR NR 15.98% 0.00% 63.36% 20.43% 7.69% 71.77% 23.04% NR 8.06% 41.24% 0.23% NR 87.47% 60.66%
IX Resin fraction 43.06% 62.12% 53.58% 0.54% 22.10% 93.91% 29.47% 23.43% 90.28% 95.63% 5.35% NR 0.00% 0.08% 0.00% 0.00% 42.37% 5.18% 0.04% 0.12% 0.00% NR 55.24% 45.56% 38.04% NR NR NR 19.53% 83.67% 0.00% #DIV/0! 0.00% 61.81% 76.38% 0.00% 72.52% 63.57% 0.12% NR NR NR 0.23% 0.00% 34.99% 4.19% 25.51% 0.00% 38.40% NR 0.00% 16.62% 93.95% NR 0.01% 0.38%
LAW and HLW Carbon Bed fraction 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 98.32% 0.00% 100.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% 0.00% #DIV/0! 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0.00% 0.00% NR 0.00% 0.00%
Other Debris fraction 52.41% 20.48% 28.53% 37.37% 71.47% 5.95% 65.36% 25.78% 9.52% 4.37% 0.47% NR 100.00% 0.01% 55.78% 0.00% 1.17% 86.96% 8.12% 30.78% 87.21% NR 4.08% 50.24% 48.83% NR NR NR 19.42% 15.31% 0.00% #DIV/0! 91.91% 32.59% 18.58% 21.65% 22.06% 5.08% 58.40% NR NR NR 83.79% 100.00% 1.65% 75.39% 66.80% 28.23% 38.56% NR 91.94% 42.15% 5.83% NR 12.52% 38.96%
HLW Silver Mordenite Absorbent fraction 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 1.59% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% 0.00% #DIV/0! 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0.00% 0.00% NR 0.00% 0.00%
WTP SSW INVENTORY Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
HEPA Filters Debris 3.43E-03 3.79E+00 4.04E-02 1.79E+01 1.86E-03 8.13E-08 1.29E-03 1.82E-01 1.73E-06 0.00E+00 7.02E+02 NR 0.00E+00 1.68E-01 5.76E-02 0.00E+00 1.76E+02 6.87E-08 1.05E-01 6.02E-03 1.09E-02 NR 1.86E+03 1.27E-06 5.77E-02 NR NR NR 7.23E+00 2.45E-06 0.00E+00 #DIV/0! 2.30E-05 5.91E-05 3.96E-08 6.38E-03 6.12E-04 1.26E-01 8.33E-02 NR NR NR 5.70E-03 0.00E+00 6.14E-01 6.18E-03 3.89E-06 2.05E-04 3.42E-05 NR 1.11E-04 1.17E-05 1.05E-06 NR 1.36E-01 1.93E-02
IX Resin Non-Debris 3.26E-02 1.35E+01 1.21E-01 1.54E-01 6.39E-03 5.22E-05 7.38E-03 8.39E-02 7.54E-04 7.70E+04 3.99E+01 NR 0.00E+00 8.98E+01 5.19E-07 2.34E-02 1.32E+02 4.53E-08 4.16E-05 1.01E-05 1.87E-08 NR 2.53E+03 1.38E-05 1.67E-01 NR NR NR 2.31E+00 1.99E-04 0.00E+00 #DIV/0! 5.94E-09 6.51E-04 6.00E-07 1.20E-08 8.18E-03 2.55E-01 2.39E-04 NR NR NR 8.18E-05 0.00E+00 3.39E-01 1.27E-03 1.29E-05 4.95E-12 5.70E-05 NR 1.37E-09 4.72E-06 4.35E-04 NR 1.21E-05 1.21E-04
LAW and HLW Carbon Beds Non-Debris 8.72E-13 2.55E-09 5.69E-11 1.33E-08 2.51E-13 1.24E-15 2.04E-13 2.72E-10 1.74E-14 4.22E-02 7.29E-10 NR 0.00E+00 1.05E+05 3.43E-11 1.05E+03 1.07E-07 1.52E-18 6.31E-11 3.62E-12 1.08E-11 NR 1.18E-06 3.26E-16 5.17E-11 NR NR NR 5.37E-09 4.75E-15 0.00E+00 #DIV/0! 3.19E-16 3.36E-14 3.16E-17 1.82E-11 7.37E-13 1.32E-10 4.99E-11 NR NR NR 1.01E-11 0.00E+00 3.79E-10 1.01E-11 1.06E-15 1.23E-13 1.59E-14 NR 1.56E-15 6.97E-15 1.03E-14 NR 8.11E-11 1.16E-11
Other Debris Debris 3.97E-02 4.46E+00 6.45E-02 1.08E+01 2.07E-02 3.31E-06 1.64E-02 9.23E-02 7.95E-05 3.51E+03 3.49E+00 NR 3.26E-03 5.57E+00 7.26E-02 2.10E-03 3.65E+00 7.61E-07 9.28E-03 2.68E-03 7.40E-02 NR 1.87E+02 1.52E-05 2.15E-01 NR NR NR 2.30E+00 3.64E-05 0.00E+00 #DIV/0! 2.62E-04 3.43E-04 1.46E-07 1.76E-03 2.49E-03 2.04E-02 1.17E-01 NR NR NR 2.99E-02 2.27E-07 1.60E-02 2.28E-02 3.38E-05 8.05E-05 5.73E-05 NR 1.27E-03 1.20E-05 2.70E-05 NR 1.94E-02 1.24E-02
HLW Silver Mordenite Absorbent Non-Debris 7.01E-14 8.38E-11 8.35E-11 1.53E-10 1.01E-13 1.66E-19 2.89E-14 4.15E-10 5.65E-17 2.18E-07 6.13E-10 NR 0.00E+00 1.69E+03 2.54E-13 8.26E-03 1.55E-09 9.49E-19 1.31E-13 2.34E-14 1.87E-11 NR 2.02E-09 1.81E-17 5.61E-11 NR NR NR 2.74E-09 6.26E-17 0.00E+00 #DIV/0! 6.38E-16 1.42E-15 3.63E-19 3.64E-11 7.29E-13 1.31E-10 2.06E-13 NR NR NR 2.02E-11 0.00E+00 3.19E-13 1.99E-11 7.50E-17 8.73E-16 1.86E-15 NR 3.11E-15 5.24E-17 3.11E-19 NR 1.44E-15 4.23E-14
SSW Total 7.57E-02 2.18E+01 2.26E-01 2.88E+01 2.89E-02 5.56E-05 2.50E-02 3.58E-01 8.35E-04 8.05E+04 7.46E+02 NR 3.26E-03 1.06E+05 1.30E-01 1.05E+03 3.11E+02 8.75E-07 1.14E-01 8.72E-03 8.48E-02 NR 4.58E+03 3.02E-05 4.40E-01 NR NR NR 1.18E+01 2.38E-04 0.00E+00 #DIV/0! 2.85E-04 1.05E-03 7.86E-07 8.14E-03 1.13E-02 4.01E-01 2.01E-01 NR NR NR 3.57E-02 2.27E-07 9.70E-01 3.03E-02 5.06E-05 2.85E-04 1.49E-04 NR 1.38E-03 2.84E-05 4.63E-04 NR 1.55E-01 3.19E-02
BBI 5.91E+05 1.99E+03 8.20E+04
Check 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% N/A 100% 100% 100% 100% 100% 100% 100% 100% 100% N/A 100% 100% 100% N/A N/A N/A 100% 100% 0% #DIV/0! 100% 100% 100% 100% 100% 100% 100% N/A N/A N/A 100% 100% 100% 100% 100% 100% 100% N/A 100% 100% 100% N/A 100% 100%
SE
CT
ION
1S
EC
TIO
N 2
SE
CT
ION
3A
SE
CT
ION
4S
EC
TIO
N 5
A
RPP-ENV-58562 Rev.03 5/9/2016 - 11:21 AM 105 of 118RPP-ENV-58562 Rev.03 9/26/2016 - 12:49 PM 105 of 124
RPP-ENV-58562, Rev. 3
A-15/A-16
Table A-7. Run Case 10A Radionuclides.
SVF-4096, IDF PA Case 10A - Single Pass Tc_Tc-99 Retention in ILAW Glass of 32% - Mass Balance, MMR-50053
WASTE STREAM 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
LAW Glass Subtotal (IDF) 1.17E+01 3.59E+03 3.10E+03 3.84E+02 5.70E+00 1.50E-01 7.84E+03 7.40E+03 0.00E+00 1.44E-01 5.71E-05 5.79E-04 7.40E-04 7.10E-03 1.33E+01 1.87E+02 2.77E-08 5.54E-08 6.31E-08 1.34E-01 9.02E+00 3.03E+00 1.23E-01 9.40E-02 1.70E+01 2.31E+02 2.73E+00 4.29E+03 9.16E+02 5.92E+03 7.21E+03 1.20E+02 7.25E-02 2.99E+00 1.32E+01 2.92E+02 0.00E+00 4.98E+01 1.20E-04 4.45E+03 1.08E+02 2.14E+05 2.14E+05 5.24E-04 3.67E-04 8.45E+03
LAW Spent Melter Subtotal (IDF) 1.25E-02 4.82E+00 2.77E+00 5.44E-01 7.67E-03 1.76E-04 1.03E+01 9.76E+00 0.00E+00 1.35E-04 5.35E-08 5.43E-07 6.95E-07 9.34E-06 1.87E-02 2.78E-01 2.60E-11 5.19E-11 5.92E-11 1.65E-04 1.24E-02 4.21E-03 1.71E-04 1.27E-04 2.40E-02 3.17E-01 3.80E-03 5.97E+00 1.26E+00 6.90E+00 9.63E+00 1.68E-01 9.56E-05 3.54E-03 1.97E-02 4.35E-01 0.00E+00 7.40E-02 1.12E-07 6.65E+00 1.46E-01 2.27E+02 2.27E+02 4.91E-07 3.45E-07 1.13E+01
ETF Solid Waste Form to IDF 2.31E-01 3.86E+01 1.01E+03 4.35E+00 1.87E+01 4.82E-02 2.51E+03 2.37E+03 2.53E+00 1.33E-03 5.19E-07 5.47E-06 6.81E-06 2.31E-03 1.56E-01 6.10E+01 2.52E-10 5.77E-10 5.73E-10 1.22E-03 8.20E-02 3.04E-02 1.24E-03 8.87E-04 1.54E-01 2.10E+00 2.76E-02 3.89E+01 8.32E+00 1.17E+02 6.55E+01 1.32E+00 8.35E-04 5.79E-02 1.45E-01 3.21E+00 2.75E+00 5.00E-01 8.67E-05 4.47E+01 3.53E+01 2.01E+03 2.01E+03 3.11E-07 5.66E-03 1.80E+04
Solid Waste Forms from Treatment Processes (IDF) 6.32E-05 7.10E-03 1.00E-02 1.79E-02 4.37E+00 7.51E-02 3.75E+03 3.54E+03 0.00E+00 2.68E-03 6.79E-07 4.09E-05 2.03E-05 2.70E-08 1.42E-06 7.12E-04 1.19E-09 3.97E-09 5.54E-09 2.13E-08 1.50E-06 5.01E-07 2.04E-08 1.51E-08 1.89E-06 1.02E-02 4.53E-07 1.86E-02 1.82E-02 9.84E-03 8.32E-04 3.67E-04 8.32E-09 7.64E-07 6.13E-04 9.79E-04 0.00E+00 4.09E-04 1.68E-05 3.66E-02 4.16E-03 2.62E+01 2.62E+01 2.66E-04 -9.51E-04 1.37E+01
Non-IDF Stream 2.65E-03 1.92E+02 4.92E-01 1.31E-01 5.02E-01 7.12E+02 3.87E+07 3.65E+07 8.25E+02 3.20E+06 8.10E+02 4.88E+04 2.42E+04 8.21E-06 -8.62E+00 -2.33E+02 1.42E+00 4.74E+00 6.61E+00 8.19E+00 6.37E+02 2.13E+02 8.71E+00 6.03E+00 8.99E+01 2.24E+03 1.93E+02 4.29E+04 9.07E+03 1.42E+05 7.13E+04 7.13E-02 6.75E-01 6.39E+01 4.86E-03 1.06E-01 2.80E+03 1.39E+03 3.72E+03 1.25E+05 -3.15E-03 4.35E+07 4.35E+07 3.34E+03 2.83E+03 5.47E+00
BBI 1.20E+01 3.89E+03 4.13E+03 3.91E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 5.51E+02 3.57E+06 9.07E+02 5.30E+04 2.55E+04 9.95E-03 4.14E+00 6.77E+00 1.48E+00 5.16E+00 6.77E+00 8.87E+00 6.82E+02 2.37E+02 9.71E+00 6.50E+00 1.15E+02 2.63E+03 2.15E+02 4.94E+04 1.08E+04 1.57E+05 8.38E+04 1.22E+02 8.26E-01 7.23E+01 1.35E+01 2.98E+02 2.82E+03 1.62E+03 4.10E+03 1.44E+05 1.44E+02 4.76E+07 4.76E+07 3.73E+03 3.17E+03 2.65E+04
HTWOS Feed 1.20E+01 3.89E+03 4.13E+03 3.91E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 8.28E+02 3.57E+06 9.07E+02 5.30E+04 2.55E+04 9.95E-03 4.14E+00 6.77E+00 1.48E+00 5.16E+00 6.77E+00 8.87E+00 6.82E+02 2.37E+02 9.71E+00 6.50E+00 1.15E+02 2.64E+03 2.16E+02 5.14E+04 1.09E+04 1.57E+05 8.39E+04 1.22E+02 8.27E-01 7.23E+01 1.35E+01 2.98E+02 2.82E+03 1.62E+03 4.10E+03 1.44E+05 1.44E+02 4.76E+07 4.76E+07 3.73E+03 3.17E+03 2.65E+04
HTWOS Feed Adjusted Minus TF and TRU Accumulation 1.20E+01 3.82E+03 4.11E+03 3.90E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 8.27E+02 3.27E+06 8.25E+02 4.95E+04 2.45E+04 9.43E-03 4.56E+00 9.25E+00 1.43E+00 4.83E+00 6.63E+00 8.39E+00 6.51E+02 2.19E+02 8.94E+00 6.20E+00 1.08E+02 2.51E+03 1.99E+02 4.82E+04 1.02E+04 1.50E+05 7.99E+04 1.21E+02 7.62E-01 6.79E+01 1.34E+01 2.96E+02 2.81E+03 1.48E+03 3.80E+03 1.33E+05 1.44E+02 4.41E+07 4.41E+07 3.48E+03 2.95E+03 2.65E+04
ACCUMULATION STREAM 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
PT-Accumulation 1.89E-04 2.25E+00 1.15E-01 5.62E-02 3.46E-02 1.27E+00 2.79E+05 2.64E+05 1.47E-01 6.56E+04 1.45E+01 7.07E+02 2.88E+02 1.19E-06 -2.99E-01 -6.06E+00 9.63E-03 9.08E-02 2.61E-02 6.32E-02 4.38E+00 2.47E+00 1.03E-01 6.42E-02 1.19E+00 3.82E+01 2.31E+00 9.12E+02 1.92E+02 1.70E+03 1.23E+03 1.13E-02 1.34E-02 8.83E-01 1.07E-03 2.35E-02 1.98E+00 3.55E+01 7.75E+01 3.08E+03 2.26E-02 3.32E+05 3.32E+05 1.30E+02 1.13E+02 3.64E+00
TF-Accumulation 9.34E-06 6.76E+01 2.11E+01 1.97E+00 7.67E-02 2.40E-02 1.88E+04 1.77E+04 2.25E-01 3.02E+05 8.15E+01 3.50E+03 1.06E+03 5.21E-04 -4.12E-01 -2.49E+00 4.72E-02 3.29E-01 1.34E-01 4.80E-01 3.07E+01 1.78E+01 7.65E-01 3.02E-01 6.46E+00 1.24E+02 1.72E+01 3.24E+03 6.86E+02 6.72E+03 4.01E+03 9.33E-01 6.50E-02 4.37E+00 1.39E-01 2.52E+00 4.69E+00 1.38E+02 3.06E+02 1.18E+04 5.14E-02 3.54E+06 3.54E+06 2.55E+02 2.20E+02 8.99E+00
TRU-Accumulation 3.92E-14 5.50E-04 3.41E-06 6.30E-05 6.28E-06 1.86E-09 2.64E+00 2.50E+00 8.33E-04 1.13E+00 3.05E-05 1.77E-02 7.06E-03 7.63E-08 1.47E-06 4.74E-12 2.31E-10 4.67E-06 1.94E-12 6.29E-08 5.45E-09 7.26E-03 2.34E-04 7.01E-05 2.54E-05 2.82E-02 5.37E-03 2.23E+00 2.70E-01 3.27E-01 7.48E-01 5.56E-05 1.33E-05 3.19E-05 5.76E-07 1.22E-05 3.85E-03 1.44E-04 5.41E-04 1.94E-02 3.44E-05 3.34E+01 3.34E+01 1.89E-02 1.73E-02 1.18E-02
LAW Accumulation 5.49E-05 3.78E-01 3.57E-02 1.39E-02 1.38E-03 2.11E-06 3.85E-01 3.64E-01 2.24E-02 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.30E-07 2.57E-03 1.23E-01 0.00E+00 0.00E+00 0.00E+00 7.24E-06 5.04E-04 2.77E-04 1.16E-05 7.37E-06 5.50E-04 1.06E-02 2.59E-04 2.54E-01 5.35E-02 1.91E-01 3.41E-01 3.06E-03 3.72E-06 1.27E-04 2.95E-04 6.52E-03 4.54E-02 1.15E-02 0.00E+00 9.98E-01 6.51E-03 1.12E+02 1.12E+02 0.00E+00 0.00E+00 1.47E+00
HLW-Accumulation 2.86E-08 2.45E-03 5.74E-05 2.70E-05 9.60E-04 4.69E-02 1.19E+04 1.12E+04 1.58E-05 3.40E+03 7.53E-01 3.72E+01 1.52E+01 4.95E-10 -1.58E-02 -3.85E-01 5.43E-04 4.73E-03 1.56E-03 3.37E-03 2.38E-01 1.28E-01 5.34E-03 3.40E-03 5.88E-02 1.97E+00 1.19E-01 4.65E+01 9.82E+00 8.74E+01 6.28E+01 5.87E-06 6.86E-04 4.50E-02 5.63E-07 1.24E-05 5.14E+00 1.74E+00 4.02E+00 1.50E+02 8.62E-06 1.71E+04 1.71E+04 6.76E+00 5.50E+00 2.63E-04
SLAW-Accumulation 6.52E-05 6.36E-01 3.83E-02 1.72E-02 1.54E-03 2.28E-06 4.20E-01 3.97E-01 3.60E-02 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.66E-07 3.11E-03 1.15E-01 0.00E+00 0.00E+00 0.00E+00 1.09E-05 7.43E-04 4.39E-04 1.84E-05 1.12E-05 6.87E-04 1.68E-02 4.12E-04 4.06E-01 8.57E-02 2.26E-01 5.44E-01 3.85E-03 5.96E-06 1.53E-04 3.48E-04 7.68E-03 4.24E-02 2.11E-02 0.00E+00 1.84E+00 7.25E-03 2.30E+02 2.30E+02 0.00E+00 0.00E+00 1.47E+00
LAWPS-Accumulation 3.89E-07 2.29E-03 3.26E-04 8.13E-04 3.30E-05 1.22E-04 3.89E+01 3.68E+01 2.84E-04 0.00E+00 0.00E+00 0.00E+00 0.00E+00 5.15E-09 8.93E-06 1.39E-05 0.00E+00 0.00E+00 0.00E+00 6.88E-08 4.39E-06 2.72E-06 1.08E-07 1.77E-07 6.04E-06 7.78E-05 2.16E-06 1.32E-03 3.29E-04 1.55E-03 3.80E-03 1.72E-05 3.04E-08 1.02E-06 1.94E-06 4.15E-05 5.94E-04 7.48E-05 0.00E+00 6.79E-03 1.40E-04 2.47E-01 2.47E-01 0.00E+00 0.00E+00 3.38E-02
ETF-Accumulation 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00
LERF-Accumulation 2.22E-05 1.62E-01 1.71E-01 4.43E-03 1.82E-02 8.82E-06 1.86E+00 1.76E+00 3.29E-03 4.08E-18 1.62E-21 1.64E-20 2.10E-20 1.74E-06 7.31E-04 5.18E-01 7.85E-25 1.57E-24 1.79E-24 2.03E-06 1.42E-04 7.82E-05 3.27E-06 2.05E-06 1.24E-04 3.95E-03 7.31E-05 8.53E-02 1.81E-02 9.07E-02 1.19E-01 9.62E-04 2.08E-06 5.96E-05 9.05E-05 2.00E-03 2.75E+00 4.81E-03 3.38E-21 4.17E-01 3.37E-02 1.96E+01 1.96E+01 3.35E-22 6.39E-20 1.54E+01
Total Accumulation 3.41E-04 7.10E+01 2.15E+01 2.06E+00 1.33E-01 1.34E+00 3.10E+05 2.93E+05 4.35E-01 3.71E+05 9.67E+01 4.25E+03 1.36E+03 5.24E-04 -7.21E-01 -8.17E+00 5.74E-02 4.25E-01 1.61E-01 5.46E-01 3.54E+01 2.04E+01 8.74E-01 3.70E-01 7.71E+00 1.64E+02 1.97E+01 4.20E+03 8.89E+02 8.51E+03 5.30E+03 9.52E-01 7.92E-02 5.30E+00 1.40E-01 2.56E+00 1.47E+01 1.76E+02 3.88E+02 1.50E+04 1.22E-01 3.89E+06 3.89E+06 3.92E+02 3.38E+02 3.10E+01
Accumulation minus TF and TRU 3.32E-04 3.43E+00 3.61E-01 9.26E-02 5.67E-02 1.31E+00 2.91E+05 2.75E+05 2.09E-01 6.90E+04 1.52E+01 7.44E+02 3.03E+02 3.64E-06 -3.08E-01 -5.69E+00 1.02E-02 9.55E-02 2.77E-02 6.66E-02 4.62E+00 2.59E+00 1.09E-01 6.76E-02 1.25E+00 4.02E+01 2.43E+00 9.59E+02 2.02E+02 1.79E+03 1.29E+03 1.92E-02 1.41E-02 9.28E-01 1.80E-03 3.98E-02 9.97E+00 3.73E+01 8.16E+01 3.23E+03 7.02E-02 3.50E+05 3.50E+05 1.37E+02 1.18E+02 2.20E+01
ADJUSTED INVENTORY TO INCLUDE ACCUMULATION-Radionuclides decayed to 1/1/2008 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
LAW Glass Subtotal (IDF) 1.17E+01 3.59E+03 3.10E+03 3.84E+02 5.71E+00 1.51E-01 7.89E+03 7.45E+03 0.00E+00 1.47E-01 5.81E-05 5.88E-04 7.50E-04 7.10E-03 1.24E+01 7.20E+01 2.79E-08 5.65E-08 6.33E-08 1.36E-01 9.08E+00 3.07E+00 1.25E-01 9.50E-02 1.72E+01 2.35E+02 2.77E+00 4.37E+03 9.34E+02 5.99E+03 7.33E+03 1.20E+02 7.38E-02 3.03E+00 1.32E+01 2.92E+02 0.00E+00 5.11E+01 1.22E-04 4.56E+03 1.08E+02 2.15E+05 2.15E+05 5.44E-04 3.82E-04 8.46E+03
LAW Spent Melter Subtotal (IDF) 1.25E-02 4.82E+00 2.77E+00 5.44E-01 7.68E-03 1.77E-04 1.04E+01 9.83E+00 0.00E+00 1.38E-04 5.45E-08 5.51E-07 7.03E-07 9.35E-06 1.75E-02 1.07E-01 2.62E-11 5.30E-11 5.94E-11 1.66E-04 1.25E-02 4.26E-03 1.73E-04 1.29E-04 2.43E-02 3.22E-01 3.84E-03 6.09E+00 1.29E+00 6.99E+00 9.78E+00 1.68E-01 9.74E-05 3.59E-03 1.97E-02 4.35E-01 0.00E+00 7.59E-02 1.15E-07 6.81E+00 1.46E-01 2.29E+02 2.29E+02 5.11E-07 3.58E-07 1.13E+01
ETF Solid Waste Form to IDF 2.31E-01 3.86E+01 1.01E+03 4.35E+00 1.88E+01 4.83E-02 2.53E+03 2.39E+03 2.53E+00 1.35E-03 5.29E-07 5.55E-06 6.90E-06 2.32E-03 1.46E-01 2.35E+01 2.54E-10 5.89E-10 5.75E-10 1.23E-03 8.25E-02 3.08E-02 1.26E-03 8.97E-04 1.56E-01 2.13E+00 2.79E-02 3.97E+01 8.49E+00 1.18E+02 6.66E+01 1.32E+00 8.51E-04 5.87E-02 1.45E-01 3.21E+00 2.76E+00 5.12E-01 8.85E-05 4.58E+01 3.53E+01 2.02E+03 2.02E+03 3.23E-07 5.88E-03 1.80E+04
Solid Waste Forms from Treatment Processes (IDF) 6.32E-05 7.11E-03 1.00E-02 1.79E-02 4.38E+00 7.52E-02 3.78E+03 3.56E+03 0.00E+00 2.74E-03 6.92E-07 4.15E-05 2.05E-05 2.70E-08 1.32E-06 2.74E-04 1.20E-09 4.05E-09 5.56E-09 2.14E-08 1.51E-06 5.07E-07 2.07E-08 1.53E-08 1.91E-06 1.04E-02 4.58E-07 1.89E-02 1.86E-02 9.96E-03 8.45E-04 3.67E-04 8.47E-09 7.75E-07 6.13E-04 9.79E-04 0.00E+00 4.19E-04 1.72E-05 3.75E-02 4.17E-03 2.64E+01 2.64E+01 2.77E-04 -9.89E-04 1.37E+01
Non-IDF Stream 2.65E-03 1.92E+02 4.92E-01 1.31E-01 5.03E-01 7.13E+02 3.90E+07 3.68E+07 8.25E+02 3.26E+06 8.25E+02 4.95E+04 2.45E+04 8.21E-06 -8.04E+00 -8.99E+01 1.43E+00 4.83E+00 6.63E+00 8.25E+00 6.42E+02 2.16E+02 8.82E+00 6.10E+00 9.10E+01 2.28E+03 1.96E+02 4.37E+04 9.25E+03 1.44E+05 7.24E+04 7.13E-02 6.87E-01 6.48E+01 4.86E-03 1.06E-01 2.81E+03 1.43E+03 3.80E+03 1.28E+05 -3.15E-03 4.38E+07 4.38E+07 3.47E+03 2.95E+03 5.47E+00
TOTAL 1.20E+01 3.82E+03 4.11E+03 3.90E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 8.27E+02 3.26E+06 8.25E+02 4.95E+04 2.45E+04 9.43E-03 4.53E+00 5.75E+00 1.43E+00 4.83E+00 6.63E+00 8.39E+00 6.51E+02 2.19E+02 8.94E+00 6.19E+00 1.08E+02 2.51E+03 1.99E+02 4.82E+04 1.02E+04 1.50E+05 7.98E+04 1.21E+02 7.62E-01 6.79E+01 1.34E+01 2.96E+02 2.81E+03 1.48E+03 3.80E+03 1.32E+05 1.44E+02 4.41E+07 4.41E+07 3.47E+03 2.95E+03 2.65E+04
100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 161% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100%
ADJUSTED INVENTORY TO INCLUDE ACCUMULATION-Radionuclides decayed to 1/1/2051 IDF Waste Streams Only 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
LAW Glass Subtotal (IDF) 2.39E-12 4.33E+02 6.28E-02 3.84E+02 5.71E+00 8.12E-08 2.93E+03 2.77E+03 0.00E+00 1.06E-01 6.43E-06 1.83E-05 1.41E-06 6.97E-03 3.16E+00 4.08E-01 2.78E-08 5.64E-08 6.33E-08 8.84E-02 9.08E+00 3.07E+00 1.25E-01 9.50E-02 1.72E+01 1.67E+02 2.77E+00 4.37E+03 9.30E+02 5.80E+03 9.25E+02 9.68E+01 7.38E-02 3.02E+00 4.74E+00 5.62E+01 0.00E+00 5.10E+01 4.27E-07 3.40E+03 1.08E+02 7.64E+04 7.64E+04 5.44E-04 5.19E-04 8.45E+03
LAW Spent Melter Subtotal (IDF) 2.54E-15 5.82E-01 5.62E-05 5.44E-01 7.68E-03 9.51E-11 3.87E+00 3.65E+00 0.00E+00 9.91E-05 6.03E-09 1.72E-08 1.32E-09 9.17E-06 4.44E-03 6.05E-04 2.61E-11 5.29E-11 5.94E-11 1.09E-04 1.25E-02 4.26E-03 1.73E-04 1.29E-04 2.43E-02 2.29E-01 3.84E-03 6.08E+00 1.28E+00 6.79E+00 1.23E+00 1.36E-01 9.74E-05 3.58E-03 7.09E-03 8.39E-02 0.00E+00 7.59E-02 4.01E-10 5.07E+00 1.46E-01 8.13E+01 8.13E+01 5.11E-07 4.87E-07 1.13E+01
ETF Solid Waste Form to IDF 4.70E-14 4.67E+00 2.04E-02 4.35E+00 1.88E+01 2.60E-08 9.39E+02 8.87E+02 2.51E+00 9.72E-04 5.85E-08 1.73E-07 1.30E-08 2.27E-03 3.71E-02 1.33E-01 2.53E-10 5.88E-10 5.75E-10 8.03E-04 8.25E-02 3.08E-02 1.26E-03 8.97E-04 1.56E-01 1.52E+00 2.79E-02 3.97E+01 8.45E+00 1.12E+02 8.41E+00 1.07E+00 8.51E-04 5.85E-02 5.21E-02 6.18E-01 2.46E-01 5.12E-01 3.10E-07 3.41E+01 3.53E+01 7.18E+02 7.18E+02 3.23E-07 9.24E-04 1.80E+04
Solid Waste Forms from Treatment Processes (IDF) 1.29E-17 8.59E-04 2.03E-07 1.79E-02 4.38E+00 4.05E-08 1.40E+03 1.32E+03 0.00E+00 1.97E-03 7.65E-08 1.29E-06 3.87E-08 2.65E-08 3.39E-07 1.56E-06 1.19E-09 4.05E-09 5.56E-09 1.40E-08 1.51E-06 5.07E-07 2.07E-08 1.53E-08 1.91E-06 7.40E-03 4.58E-07 1.89E-02 1.85E-02 9.32E-03 1.07E-04 2.97E-04 8.47E-09 7.72E-07 2.20E-04 1.89E-04 0.00E+00 4.19E-04 6.02E-08 2.79E-02 4.17E-03 9.36E+00 9.36E+00 2.77E-04 7.79E-05 1.37E+01
SSW FRACTIONS BASED ON 10-010 and 10-009 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
HEPA fraction NR NR NR 51.81% 1.03% 52.45% 50.81% NR 10.40% NR 65.24% 64.99% 65.27% NR NR NR NR NR NR NR 68.98% 68.94% 68.90% 68.85% 54.86% 68.68% 68.39% 68.53% 68.48% 70.74% 68.04% NR NR NR NR NR 0.01% 56.98% 62.75% 57.75% 71.82% 65.75% NR NR NR 87.60%
IX Resin fraction NR NR NR 43.80% 0.14% 8.96% 9.27% NR 1.53% NR 7.64% 7.67% 7.61% NR NR NR NR NR NR NR 0.00% 0.00% 0.00% 0.00% 42.37% 0.00% 0.00% 0.00% 0.00% 3.83% 0.00% NR NR NR NR NR 49.09% 20.28% 19.08% 19.89% 26.01% 0.09% NR NR NR 11.86%
LAW and HLW Carbon Bed fraction NR NR NR 0.00% 36.47% 0.00% 0.00% NR 34.07% NR 0.00% 0.00% 0.00% NR NR NR NR NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR NR NR 36.25% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00%
Other Debris fraction NR NR NR 4.39% 0.01% 38.59% 39.92% NR 24.63% NR 27.13% 27.34% 27.12% NR NR NR NR NR NR NR 31.02% 31.06% 31.10% 31.15% 2.77% 31.32% 31.61% 31.47% 31.52% 25.43% 31.96% NR NR NR NR NR 14.62% 22.75% 18.17% 22.35% 2.17% 34.16% NR NR NR 0.54%
HLW Silver Mordenite Absorbent fraction NR NR NR 0.00% 62.35% 0.00% 0.00% NR 29.36% NR 0.00% 0.00% 0.00% NR NR NR NR NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR NR NR 0.03% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00%
WTP SSW INVENTORY-Radionuclides decayed to 1/1/2008 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
HEPA Filters Debris NR NR NR 9.29E-03 4.52E-02 3.94E-02 1.92E+03 NR 0.00E+00 NR 4.51E-07 2.70E-05 1.34E-05 NR NR NR NR NR NR NR 1.04E-06 3.49E-07 1.42E-08 1.05E-08 1.05E-06 7.14E-03 3.13E-07 1.30E-02 1.27E-02 7.05E-03 5.75E-04 NR NR NR NR NR 0.00E+00 2.39E-04 1.08E-05 2.17E-02 2.99E-03 1.73E+01 NR NR NR 1.20E+01
IX Resin Non-Debris NR NR NR 7.86E-03 5.99E-03 6.74E-03 3.50E+02 NR 0.00E+00 NR 5.28E-08 3.18E-06 1.56E-06 NR NR NR NR NR NR NR 5.07E-13 1.75E-13 6.05E-15 7.16E-15 8.10E-07 7.52E-08 1.60E-13 1.38E-07 1.36E-07 3.81E-04 6.25E-09 NR NR NR NR NR 0.00E+00 8.50E-05 3.28E-06 7.46E-03 1.08E-03 2.47E-02 NR NR NR 1.63E+00
LAW and HLW Carbon Beds Non-Debris NR NR NR 1.86E-13 1.60E+00 1.40E-11 5.95E-07 NR 0.00E+00 NR 1.43E-18 8.93E-17 4.37E-17 NR NR NR NR NR NR NR 5.65E-19 2.10E-19 8.82E-21 8.12E-21 1.92E-17 4.00E-15 1.92E-19 7.35E-15 7.19E-15 1.33E-14 3.31E-16 NR NR NR NR NR 0.00E+00 1.75E-14 1.11E-16 1.56E-12 3.03E-13 3.06E-09 NR NR NR 1.81E-09
Other Debris Debris NR NR NR 7.87E-04 3.95E-04 2.90E-02 1.51E+03 NR 0.00E+00 NR 1.88E-07 1.13E-05 5.57E-06 NR NR NR NR NR NR NR 4.69E-07 1.57E-07 6.42E-09 4.75E-09 5.29E-08 3.26E-03 1.45E-07 5.96E-03 5.86E-03 2.53E-03 2.70E-04 NR NR NR NR NR 0.00E+00 9.54E-05 3.12E-06 8.39E-03 9.05E-05 9.01E+00 NR NR NR 7.39E-02
HLW Silver Mordenite Absorbent Non-Debris NR NR NR 1.80E-16 2.73E+00 2.79E-11 1.18E-06 NR 0.00E+00 NR 3.59E-19 2.75E-17 1.32E-17 NR NR NR NR NR NR NR 1.13E-18 4.19E-19 1.76E-20 1.62E-20 1.25E-20 8.00E-15 3.84E-19 1.47E-14 1.44E-14 7.81E-15 6.63E-16 NR NR NR NR NR 0.00E+00 2.81E-14 2.38E-17 2.51E-12 3.72E-14 6.11E-09 NR NR NR 1.53E-12
SSW Total NR NR NR 1.79E-02 4.38E+00 7.52E-02 3.78E+03 NR 0.00E+00 NR 6.92E-07 4.15E-05 2.05E-05 NR NR NR NR NR NR NR 1.51E-06 5.07E-07 2.07E-08 1.53E-08 1.91E-06 1.04E-02 4.58E-07 1.89E-02 1.86E-02 9.96E-03 8.45E-04 NR NR NR NR NR 0.00E+00 4.19E-04 1.72E-05 3.75E-02 4.17E-03 2.64E+01 NR NR NR 1.37E+01
BBI 2.94E+01 3.90E+07 4.76E+07 2.65E+04
Check N/A N/A N/A 100% 100% 100% 100% N/A #DIV/0! N/A 100% 100% 100% N/A N/A N/A N/A N/A N/A N/A 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% N/A N/A N/A N/A N/A #DIV/0! 100% 100% 100% 100% 100% N/A N/A N/A 100%
WTP SSW INVENTORY-Radionuclides decayed to 1/1/2051 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
HEPA Filters Debris NR NR NR 9.29E-03 4.52E-02 2.13E-08 7.12E+02 6.72E+02 0.00E+00 0.00E+00 4.99E-08 8.40E-07 2.52E-08 NR NR NR NR NR NR NR 1.04E-06 3.49E-07 1.42E-08 1.05E-08 1.05E-06 5.08E-03 3.13E-07 1.30E-02 1.27E-02 6.59E-03 7.26E-05 NR NR NR NR NR 0.00E+00 2.39E-04 3.77E-08 1.61E-02 2.99E-03 6.15E+00 NR NR NR 1.20E+01
IX Resin Non-Debris NR NR NR 7.85E-03 5.99E-03 3.63E-09 1.30E+02 1.23E+02 0.00E+00 0.00E+00 5.85E-09 9.92E-08 2.94E-09 NR NR NR NR NR NR NR 5.06E-13 1.75E-13 6.05E-15 7.16E-15 8.10E-07 5.36E-08 1.60E-13 1.38E-07 1.35E-07 3.56E-04 7.89E-10 NR NR NR NR NR 0.00E+00 8.50E-05 1.15E-08 5.56E-03 1.08E-03 8.77E-03 NR NR NR 1.63E+00
LAW and HLW Carbon Beds Non-Debris NR NR NR 1.86E-13 1.60E+00 7.55E-18 2.21E-07 2.09E-07 0.00E+00 0.00E+00 1.58E-19 2.78E-18 8.23E-20 NR NR NR NR NR NR NR 5.65E-19 2.10E-19 8.82E-21 8.12E-21 1.92E-17 2.85E-15 1.92E-19 7.34E-15 7.15E-15 1.24E-14 4.18E-17 NR NR NR NR NR 0.00E+00 1.75E-14 3.89E-19 1.16E-12 3.03E-13 1.09E-09 NR NR NR 1.81E-09
Other Debris Debris NR NR NR 7.87E-04 3.95E-04 1.56E-08 5.59E+02 5.28E+02 0.00E+00 0.00E+00 2.08E-08 3.54E-07 1.05E-08 NR NR NR NR NR NR NR 4.68E-07 1.57E-07 6.42E-09 4.75E-09 5.29E-08 2.32E-03 1.45E-07 5.95E-03 5.83E-03 2.37E-03 3.41E-05 NR NR NR NR NR 0.00E+00 9.53E-05 1.09E-08 6.24E-03 9.04E-05 3.20E+00 NR NR NR 7.39E-02
HLW Silver Mordenite Absorbent Non-Debris NR NR NR 1.80E-16 2.73E+00 1.50E-17 4.38E-07 4.14E-07 0.00E+00 0.00E+00 3.98E-20 8.56E-19 2.48E-20 NR NR NR NR NR NR NR 1.13E-18 4.19E-19 1.76E-20 1.62E-20 1.25E-20 5.70E-15 3.84E-19 1.47E-14 1.43E-14 7.31E-15 8.36E-17 NR NR NR NR NR 0.00E+00 2.81E-14 8.32E-20 1.87E-12 3.72E-14 2.17E-09 NR NR NR 1.53E-12SE
CT
ION
5B
SE
CT
ION
1S
EC
TIO
N 2
SE
CT
ION
3A
SE
CT
ION
4S
EC
TIO
N 5
AS
EC
TIO
N 3
B
RPP-ENV-58562 Rev.03 5/9/2016 - 11:21 AM 106 of 118RPP-ENV-58562 Rev.03 9/26/2016 - 12:49 PM 106 of 124
RPP-ENV-58562, Rev. 3
A-17/A-18
Table A-8. Run Case 10A Chemicals.
SVF-4096, IDF PA Case 10A - Single Pass Tc_Tc-99 Retention in ILAW Glass of 32% - Mass Balance, MMR-50053
WASTE STREAM Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
LAW Glass Subtotal (IDF) 1.14E+03 1.96E+07 3.61E+03 1.85E+07 9.16E+00 4.92E+02 6.13E+04 7.20E+03 5.04E+04 4.09E+05 4.57E+05 4.63E-01 3.28E+02 5.80E+05 2.35E+07 0.00E+00 8.92E+05 4.59E-05 3.02E+06 5.43E+06 4.69E-05 6.39E+03 7.76E+07 3.23E+03 2.22E+03 0.00E+00 0.00E+00 0.00E+00 7.08E+04 2.11E+03 0.00E+00 0.00E+00 7.32E+01 2.69E+02 0.00E+00 3.05E+03 2.69E+03 3.88E+03 1.29E+08 0.00E+00 2.38E+06 0.00E+00 1.76E+02 6.87E-02 4.98E+02 1.66E+03 5.73E-04 7.27E+06 1.30E-04 0.00E+00 8.20E+03 7.35E-01 4.11E+03 8.84E+01 1.44E+07 1.34E+07
LAW Spent Melter Subtotal (IDF) 1.57E+00 2.66E+04 4.09E+00 2.50E+04 1.54E-02 5.93E-01 8.74E+01 7.42E+00 6.97E+01 5.64E+02 6.50E+02 6.16E-04 5.29E-01 8.46E+02 3.18E+04 0.00E+00 1.06E+03 4.30E-08 2.53E+03 7.34E+03 4.40E-08 8.30E+00 1.10E+05 4.58E+00 3.17E+00 0.00E+00 0.00E+00 0.00E+00 9.95E+01 1.47E+00 0.00E+00 0.00E+00 1.02E-01 2.36E-01 0.00E+00 2.53E+00 3.35E+00 4.39E+00 1.72E+05 0.00E+00 3.21E+03 0.00E+00 5.62E-01 1.16E-04 6.66E-01 1.78E+00 5.38E-07 9.83E+03 1.22E-07 2.44E-02 1.14E+01 1.11E-03 2.15E+00 1.22E-01 1.95E+04 1.82E+04
ETF Solid Waste Form to IDF 2.31E+01 1.14E+04 1.17E+03 1.60E+02 7.62E-01 5.81E+00 1.34E+03 6.52E+01 1.23E+03 3.68E+05 3.43E+04 9.02E-02 3.36E+01 6.05E+05 3.26E+02 1.64E+03 4.67E+04 2.73E-03 2.34E+01 1.14E+00 3.38E+01 1.37E+02 1.76E+06 3.39E+01 2.29E+01 2.82E+04 2.22E+06 8.88E+04 7.96E+03 2.15E+01 5.50E+04 0.00E+00 6.65E-01 5.58E+00 0.00E+00 3.12E+01 8.75E+02 1.26E+03 1.49E+03 0.00E+00 0.00E+00 9.32E+05 1.08E+01 1.04E-03 1.06E+03 5.45E+02 5.20E-06 1.08E-05 5.66E-05 5.19E+03 8.27E+01 8.63E-05 3.04E-03 5.71E-03 3.14E+01 1.42E-05
Solid Waste Forms from Treatment Processes (IDF) 1.01E-01 2.28E+01 2.64E-01 2.97E+01 3.61E-02 5.27E-05 2.39E-02 4.78E-01 7.40E-04 4.45E+04 6.88E+02 2.00E-01 3.22E-03 5.46E+04 1.50E-01 3.22E+02 2.96E+02 8.72E-07 1.19E-01 8.89E-03 8.36E-02 1.42E-02 4.57E+03 2.97E-05 5.83E-01 0.00E+00 0.00E+00 0.00E+00 1.23E+01 2.25E-04 3.99E+03 6.70E-07 3.80E-04 1.06E-03 7.71E-07 7.70E-03 8.68E-03 4.32E-01 1.74E-01 3.81E+03 0.00E+00 0.00E+00 3.64E-02 2.11E-07 8.10E-01 2.71E-02 5.04E-05 2.85E-04 1.45E-04 0.00E+00 1.36E-03 2.84E-05 4.39E-04 2.57E-06 1.63E-01 3.22E-02
Non-IDF Stream 2.62E+03 2.46E+06 8.75E+01 1.53E+06 8.62E+03 2.81E+00 4.83E+05 1.40E+03 6.55E+03 4.99E+03 6.68E+04 2.07E+03 2.35E+03 3.31E+04 1.39E+06 9.80E+00 1.60E+04 4.20E+04 7.28E+05 2.29E+04 4.58E+05 2.34E+01 1.94E+06 5.93E+03 1.16E+05 1.68E+07 5.74E+07 2.55E+07 2.70E+03 4.50E-01 5.07E+06 7.99E+02 7.32E+02 8.71E-02 9.20E+02 5.46E-01 1.58E+02 3.33E+01 5.42E+06 -3.81E+03 -2.38E+06 2.89E+06 6.23E+04 2.42E+02 3.22E-01 7.10E+02 6.00E+04 1.38E+03 6.63E+03 8.64E+05 5.80E+05 2.37E+03 4.37E+01 4.72E+02 4.31E+02 4.05E+05
BBI 4.03E+03 8.67E+06 4.88E+03 1.52E+04 9.42E+03 5.02E+02 5.61E+05 8.87E+03 6.96E+03 8.27E+05 5.91E+05 2.09E+03 2.91E+03 1.28E+06 1.27E+06 1.99E+03 9.57E+05 3.20E+04 1.94E+03 2.19E+04 1.64E+05 6.56E+03 4.92E+07 9.70E+03 9.87E+04 1.19E+07 5.60E+07 4.45E+06 8.20E+04 2.14E+03 5.18E+06 8.43E+02 8.45E+02 2.78E+02 9.47E+02 3.09E+03 3.73E+03 5.18E+03 8.41E+05 0.00E+00 0.00E+00 3.82E+06 4.23E+04 2.72E+02 1.56E+03 2.92E+03 6.15E+04 1.51E+03 6.98E+03 8.71E+05 6.45E+05 2.58E+03 4.16E+03 5.81E+02 6.08E+03 4.09E+05
HTWOS Feed 4.03E+03 2.26E+07 4.88E+03 2.00E+07 9.42E+03 5.02E+02 6.02E+05 8.87E+03 5.89E+04 8.28E+05 5.91E+05 2.09E+03 2.91E+03 1.28E+06 2.50E+07 1.99E+03 9.57E+05 4.47E+04 3.75E+06 5.46E+06 4.80E+05 6.56E+03 8.16E+07 9.70E+03 1.25E+05 1.68E+07 5.97E+07 2.56E+07 8.20E+04 2.14E+03 5.20E+06 8.43E+02 8.77E+02 2.78E+02 9.47E+02 3.09E+03 3.73E+03 5.18E+03 1.35E+08 0.00E+00 0.00E+00 3.83E+06 6.56E+04 2.72E+02 1.56E+03 2.92E+03 6.15E+04 7.28E+06 6.98E+03 8.71E+05 6.47E+05 2.58E+03 4.16E+03 5.81E+02 1.44E+07 1.39E+07
HTWOS Feed Adjusted Minus TF and TRU Accumulation 3.82E+03 2.22E+07 4.87E+03 2.00E+07 8.70E+03 5.02E+02 5.46E+05 8.67E+03 5.85E+04 8.28E+05 5.63E+05 2.09E+03 2.73E+03 1.28E+06 2.49E+07 1.97E+03 9.56E+05 4.22E+04 3.75E+06 5.46E+06 4.67E+05 6.55E+03 8.15E+07 9.25E+03 1.20E+05 1.68E+07 5.97E+07 2.56E+07 8.16E+04 2.13E+03 5.14E+06 8.21E+02 8.22E+02 2.75E+02 9.39E+02 3.08E+03 3.72E+03 5.18E+03 1.35E+08 0.00E+00 0.00E+00 3.82E+06 6.27E+04 2.64E+02 1.56E+03 2.91E+03 6.03E+04 7.28E+06 6.79E+03 8.70E+05 5.96E+05 2.40E+03 4.15E+03 5.70E+02 1.44E+07 1.39E+07
ACCUMULATION STREAM Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
PT-Accumulation 3.66E+01 3.47E+04 7.55E-01 1.97E+00 6.26E+01 5.52E-02 9.20E+02 2.48E+00 1.66E+02 1.05E+02 2.83E+03 1.54E+01 1.49E+01 9.94E+02 8.50E+03 3.33E-01 1.49E+02 1.44E+02 3.30E-01 2.09E+02 8.90E+03 8.26E-01 3.17E+04 5.71E+01 1.01E+03 2.96E+03 5.36E+04 5.18E+03 1.78E+01 5.61E-01 4.22E+03 2.09E+01 1.56E+01 7.57E-03 1.84E+01 6.23E-02 4.59E-01 7.55E-01 8.82E+03 0.00E+00 0.00E+00 9.77E+02 2.45E+02 2.09E+01 2.14E-01 3.56E-01 2.37E+02 1.30E+01 1.57E+02 3.07E+02 6.92E+03 2.67E+01 3.77E-02 8.95E+00 1.21E+00 2.21E+03
TF-Accumulation 2.05E+02 4.69E+05 4.23E+00 2.53E+01 7.17E+02 3.31E-01 5.49E+04 1.98E+02 4.15E+02 6.65E+02 2.82E+04 1.04E+00 1.85E+02 6.22E+03 1.11E+05 1.88E+01 4.70E+02 2.50E+03 2.69E+00 1.67E+03 1.22E+04 3.51E+00 9.30E+04 4.52E+02 5.74E+03 7.11E+03 4.55E+04 6.25E+03 4.19E+02 7.34E+00 6.54E+04 2.21E+01 5.53E+01 3.49E+00 7.92E+00 5.07E+00 2.76E+00 2.71E+00 6.94E+04 0.00E+00 0.00E+00 2.69E+03 2.93E+03 7.36E+00 5.30E-01 3.00E+00 1.21E+03 1.15E+02 1.88E+02 7.78E+02 5.16E+04 1.79E+02 2.71E+00 1.11E+01 1.93E+01 1.85E+03
TRU-Accumulation 1.94E-02 2.91E+02 1.35E-02 2.92E-01 1.55E-01 6.08E-03 3.38E+02 9.73E-02 3.47E+00 1.25E+01 1.62E+01 1.47E-04 9.11E-01 1.57E+02 1.61E+02 2.34E-03 1.66E+00 1.96E-02 7.92E-115 2.52E+00 1.11E+00 3.96E-114 1.31E+03 7.92E-114 2.02E-01 3.37E+02 1.08E+03 1.08E-01 9.32E-01 0.00E+00 1.34E+03 0.00E+00 3.72E-02 0.00E+00 0.00E+00 1.13E-20 7.22E-01 8.75E-03 1.17E+02 0.00E+00 0.00E+00 7.15E+01 1.80E+00 0.00E+00 6.93E-04 0.00E+00 1.77E-08 1.73E-01 8.36E-113 5.54E+00 1.61E+01 2.50E-62 3.60E-299 6.08E-08 2.55E+00 1.21E+00
LAW Accumulation 2.67E-01 1.49E+03 2.43E-01 9.06E+02 1.51E-02 1.53E-02 8.63E+00 3.65E-01 3.04E+00 3.62E+01 4.74E+01 2.00E-05 1.31E-02 3.75E+02 1.16E+03 1.10E-01 2.34E+01 0.00E+00 9.16E-02 2.66E+02 0.00E+00 2.29E-01 9.09E+03 4.48E-01 3.29E-01 4.35E+02 1.70E+03 2.26E+03 2.03E+00 1.57E-01 7.45E+02 0.00E+00 4.33E-03 2.12E-03 0.00E+00 1.70E-02 1.46E-01 2.46E-01 6.13E+03 3.54E-06 5.93E+01 1.33E+02 8.17E-02 5.89E-05 8.68E-02 9.88E-02 0.00E+00 3.56E+02 0.00E+00 5.08E+01 7.76E-01 1.69E-04 9.85E-03 1.39E-02 7.06E+02 6.58E+02
HLW-Accumulation 1.02E+00 1.53E+03 4.05E-04 1.02E+03 3.44E+00 3.09E-05 4.47E+01 3.04E-03 5.08E+00 8.17E-03 6.92E+01 6.55E-01 8.11E-01 7.15E-02 4.58E+02 3.86E-04 2.62E+00 7.56E+00 4.60E+02 1.12E+01 4.57E+02 4.47E-04 6.10E+02 2.36E+00 5.27E+01 1.81E+00 1.96E+02 5.27E+00 1.17E-01 2.88E-04 9.78E-02 1.06E+00 7.93E-01 3.57E-06 1.04E+00 2.91E-05 2.49E-04 3.29E-04 2.85E+03 3.86E-06 2.36E-02 3.76E-02 1.31E+01 1.07E+00 1.55E-05 1.73E-04 1.42E+01 7.19E-01 6.56E+00 7.50E-02 3.58E+02 1.40E+00 1.90E-05 4.68E-01 6.66E-04 1.30E+02
SLAW-Accumulation 3.66E-01 2.05E+03 2.61E-01 8.13E+02 1.74E-02 1.73E-02 1.28E+01 5.53E-01 8.32E+00 3.72E+01 1.58E+02 2.25E-05 1.44E-02 3.92E+02 1.05E+03 9.51E-02 2.77E+01 0.00E+00 1.05E-01 2.39E+02 0.00E+00 2.56E-01 1.41E+04 7.28E-01 5.56E-01 7.01E+02 2.79E+03 4.78E+03 2.56E+00 1.88E-01 1.28E+03 0.00E+00 6.93E-03 2.61E-03 0.00E+00 2.11E-02 1.52E-01 2.69E-01 5.51E+03 1.60E-05 3.51E+01 2.15E+02 1.54E-01 7.19E-05 8.64E-02 1.49E-01 0.00E+00 3.20E+02 0.00E+00 8.04E+01 1.23E+00 2.25E-04 1.31E-02 2.26E-02 6.33E+02 5.91E+02
LAWPS-Accumulation 6.61E-04 2.79E+00 6.69E-03 1.33E-02 3.95E-07 3.27E-04 8.51E-03 6.06E-04 0.00E+00 1.20E+00 7.40E-02 2.16E-03 5.36E-04 3.53E-01 2.91E-02 4.53E-04 1.87E+00 0.00E+00 1.51E-03 0.00E+00 0.00E+00 1.17E-02 4.83E+01 2.90E-03 1.36E-03 1.59E+01 2.86E+01 1.56E+01 1.79E-02 3.20E-05 6.68E-01 0.00E+00 2.28E-05 4.12E-06 0.00E+00 2.68E-05 4.22E-03 6.65E-03 4.54E-02 0.00E+00 0.00E+00 6.91E-01 2.18E-05 1.33E-08 1.99E-03 2.88E-05 0.00E+00 0.00E+00 0.00E+00 4.12E-01 6.47E-03 3.75E-07 7.95E-05 3.73E-06 4.77E-03 0.00E+00
ETF-Accumulation 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00
LERF-Accumulation 1.33E-01 6.50E+01 1.29E+00 1.66E-01 1.69E-03 4.76E-03 5.66E+00 1.14E-01 6.54E+00 3.08E+02 1.62E+02 6.89E-05 2.77E-02 2.86E+03 1.93E+00 1.49E+00 2.61E+01 1.30E-21 3.06E-02 4.73E-23 1.34E-21 1.24E-01 5.42E+03 1.83E-01 1.37E-01 2.01E+01 2.59E+03 1.07E+03 8.08E+00 4.94E-02 2.99E+02 0.00E+00 1.46E-03 9.76E-04 0.00E+00 5.05E-03 7.53E-01 1.29E+00 4.78E+00 0.00E+00 0.00E+00 6.50E+01 4.89E-02 1.29E-05 9.10E-01 5.74E-01 1.62E-20 8.05E-23 1.31E-19 1.79E+01 2.19E-01 8.63E-05 3.04E-03 5.70E-03 5.21E-02 1.28E-22
Total Accumulation 2.44E+02 5.09E+05 6.80E+00 2.77E+03 7.83E+02 4.30E-01 5.62E+04 2.01E+02 6.07E+02 1.16E+03 3.15E+04 1.71E+01 2.02E+02 1.10E+04 1.23E+05 2.08E+01 7.02E+02 2.65E+03 4.63E+02 2.39E+03 2.16E+04 4.96E+00 1.55E+05 5.12E+02 6.81E+03 1.16E+04 1.08E+05 1.96E+04 4.50E+02 8.30E+00 7.33E+04 4.40E+01 7.17E+01 3.51E+00 2.74E+01 5.18E+00 4.99E+00 5.29E+00 9.28E+04 2.34E-05 9.45E+01 4.15E+03 3.19E+03 2.93E+01 1.83E+00 4.17E+00 1.47E+03 8.05E+02 3.51E+02 1.24E+03 5.89E+04 2.07E+02 2.77E+00 2.06E+01 1.36E+03 5.44E+03
Accumulation minus TF and TRU 3.84E+01 3.98E+04 2.55E+00 2.75E+03 6.60E+01 9.29E-02 9.92E+02 3.51E+00 1.89E+02 4.87E+02 3.27E+03 1.60E+01 1.58E+01 4.62E+03 1.12E+04 2.03E+00 2.31E+02 1.51E+02 4.60E+02 7.25E+02 9.35E+03 1.45E+00 6.10E+04 6.08E+01 1.06E+03 4.13E+03 6.09E+04 1.33E+04 3.06E+01 9.55E-01 6.54E+03 2.20E+01 1.64E+01 1.33E-02 1.95E+01 1.05E-01 1.51E+00 2.57E+00 2.33E+04 2.34E-05 9.45E+01 1.39E+03 2.58E+02 2.20E+01 1.30E+00 1.18E+00 2.51E+02 6.90E+02 1.64E+02 4.57E+02 7.28E+03 2.81E+01 6.38E-02 9.46E+00 1.34E+03 3.59E+03
ADJUSTED INVENTORY TO INCLUDE ACCUMULATION Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
LAW Glass Subtotal (IDF) 1.15E+03 1.97E+07 3.61E+03 1.85E+07 9.23E+00 4.92E+02 6.14E+04 7.20E+03 5.06E+04 4.09E+05 4.60E+05 4.66E-01 3.29E+02 5.82E+05 2.35E+07 0.00E+00 8.92E+05 4.61E-05 3.02E+06 5.43E+06 4.78E-05 6.39E+03 7.77E+07 3.25E+03 2.24E+03 0.00E+00 0.00E+00 0.00E+00 7.08E+04 2.11E+03 0.00E+00 0.00E+00 7.46E+01 2.69E+02 0.00E+00 3.05E+03 2.69E+03 3.88E+03 1.29E+08 #DIV/0! #DIV/0! 0.00E+00 1.76E+02 7.44E-02 4.99E+02 1.66E+03 5.76E-04 7.27E+06 1.34E-04 0.00E+00 8.30E+03 7.44E-01 4.11E+03 8.99E+01 1.44E+07 1.34E+07
LAW Spent Melter Subtotal (IDF) 1.59E+00 2.66E+04 4.09E+00 2.50E+04 1.55E-02 5.93E-01 8.75E+01 7.42E+00 6.99E+01 5.64E+02 6.54E+02 6.21E-04 5.32E-01 8.49E+02 3.18E+04 0.00E+00 1.06E+03 4.32E-08 2.53E+03 7.34E+03 4.49E-08 8.30E+00 1.10E+05 4.61E+00 3.20E+00 0.00E+00 0.00E+00 0.00E+00 9.95E+01 1.47E+00 0.00E+00 0.00E+00 1.04E-01 2.36E-01 0.00E+00 2.54E+00 3.35E+00 4.40E+00 1.72E+05 #DIV/0! #DIV/0! 0.00E+00 5.64E-01 1.26E-04 6.66E-01 1.78E+00 5.40E-07 9.83E+03 1.25E-07 2.44E-02 1.15E+01 1.12E-03 2.15E+00 1.24E-01 1.95E+04 1.82E+04
ETF Solid Waste Form to IDF 2.33E+01 1.14E+04 1.17E+03 1.60E+02 7.68E-01 5.82E+00 1.34E+03 6.52E+01 1.24E+03 3.69E+05 3.45E+04 9.09E-02 3.38E+01 6.07E+05 3.26E+02 1.64E+03 4.67E+04 2.74E-03 2.34E+01 1.14E+00 3.45E+01 1.37E+02 1.76E+06 3.41E+01 2.31E+01 2.82E+04 2.22E+06 8.89E+04 7.97E+03 2.15E+01 5.50E+04 0.00E+00 6.78E-01 5.58E+00 0.00E+00 3.12E+01 8.76E+02 1.26E+03 1.49E+03 #DIV/0! #DIV/0! 9.32E+05 1.09E+01 1.13E-03 1.06E+03 5.46E+02 5.23E-06 1.08E-05 5.79E-05 5.19E+03 8.37E+01 8.73E-05 3.04E-03 5.80E-03 3.14E+01 1.42E-05
Solid Waste Forms from Treatment Processes (IDF) 1.02E-01 2.28E+01 2.64E-01 2.97E+01 3.63E-02 5.27E-05 2.39E-02 4.78E-01 7.43E-04 4.45E+04 6.92E+02 2.01E-01 3.24E-03 5.48E+04 1.50E-01 3.22E+02 2.96E+02 8.75E-07 1.19E-01 8.89E-03 8.52E-02 1.42E-02 4.57E+03 2.99E-05 5.88E-01 0.00E+00 0.00E+00 0.00E+00 1.23E+01 2.25E-04 3.99E+03 6.88E-07 3.87E-04 1.06E-03 7.87E-07 7.70E-03 8.69E-03 4.32E-01 1.74E-01 #DIV/0! #DIV/0! 0.00E+00 3.66E-02 2.28E-07 8.10E-01 2.71E-02 5.06E-05 2.85E-04 1.48E-04 0.00E+00 1.37E-03 2.87E-05 4.39E-04 2.61E-06 1.63E-01 3.22E-02
Non-IDF Stream 2.64E+03 2.46E+06 8.76E+01 1.53E+06 8.69E+03 2.81E+00 4.84E+05 1.40E+03 6.57E+03 5.00E+03 6.72E+04 2.09E+03 2.36E+03 3.32E+04 1.39E+06 9.81E+00 1.60E+04 4.22E+04 7.28E+05 2.29E+04 4.67E+05 2.34E+01 1.94E+06 5.96E+03 1.17E+05 1.68E+07 5.75E+07 2.55E+07 2.71E+03 4.50E-01 5.08E+06 8.21E+02 7.46E+02 8.71E-02 9.39E+02 5.46E-01 1.58E+02 3.33E+01 5.42E+06 #DIV/0! #DIV/0! 2.89E+06 6.25E+04 2.62E+02 3.23E-01 7.11E+02 6.03E+04 1.38E+03 6.79E+03 8.65E+05 5.87E+05 2.40E+03 4.37E+01 4.79E+02 4.31E+02 4.05E+05
TOTAL 3.82E+03 2.22E+07 4.87E+03 2.00E+07 8.70E+03 5.02E+02 5.46E+05 8.67E+03 5.85E+04 8.28E+05 5.63E+05 2.09E+03 2.73E+03 1.28E+06 2.49E+07 1.97E+03 9.56E+05 4.22E+04 3.75E+06 5.46E+06 4.67E+05 6.55E+03 8.15E+07 9.25E+03 1.20E+05 1.68E+07 5.97E+07 2.56E+07 8.16E+04 2.13E+03 5.14E+06 8.21E+02 8.22E+02 2.75E+02 9.39E+02 3.08E+03 3.72E+03 5.18E+03 1.35E+08 #DIV/0! #DIV/0! 3.82E+06 6.27E+04 2.62E+02 1.56E+03 2.91E+03 6.03E+04 7.28E+06 6.79E+03 8.70E+05 5.96E+05 2.40E+03 4.15E+03 5.69E+02 1.44E+07 1.39E+07
100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% #DIV/0! #DIV/0! 100% 100% 101% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100%
SSW FRACTIONS BASED ON 10-010 and 10-009 Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
HEPA fraction 4.53% 17.39% 17.89% 62.10% 6.43% 0.15% 5.17% 50.79% 0.21% 0.00% 94.18% NR 0.00% 0.00% 44.22% 0.00% 56.46% 7.86% 91.84% 69.10% 12.79% NR 40.68% 4.20% 13.13% NR NR NR 61.05% 1.03% 0.00% #DIV/0! 8.09% 5.61% 5.04% 78.35% 5.42% 31.35% 41.49% NR NR NR 15.98% 0.00% 63.36% 20.43% 7.69% 71.77% 23.04% NR 8.06% 41.24% 0.23% NR 87.47% 60.66%
IX Resin fraction 43.06% 62.12% 53.58% 0.54% 22.10% 93.91% 29.47% 23.43% 90.28% 95.63% 5.35% NR 0.00% 0.08% 0.00% 0.00% 42.37% 5.18% 0.04% 0.12% 0.00% NR 55.24% 45.56% 38.04% NR NR NR 19.53% 83.67% 0.00% #DIV/0! 0.00% 61.81% 76.38% 0.00% 72.52% 63.57% 0.12% NR NR NR 0.23% 0.00% 34.99% 4.19% 25.51% 0.00% 38.40% NR 0.00% 16.62% 93.95% NR 0.01% 0.38%
LAW and HLW Carbon Bed fraction 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 98.32% 0.00% 100.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% 0.00% #DIV/0! 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0.00% 0.00% NR 0.00% 0.00%
Other Debris fraction 52.41% 20.48% 28.53% 37.37% 71.47% 5.95% 65.36% 25.78% 9.52% 4.37% 0.47% NR 100.00% 0.01% 55.78% 0.00% 1.17% 86.96% 8.12% 30.78% 87.21% NR 4.08% 50.24% 48.83% NR NR NR 19.42% 15.31% 0.00% #DIV/0! 91.91% 32.59% 18.58% 21.65% 22.06% 5.08% 58.40% NR NR NR 83.79% 100.00% 1.65% 75.39% 66.80% 28.23% 38.56% NR 91.94% 42.15% 5.83% NR 12.52% 38.96%
HLW Silver Mordenite Absorbent fraction 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 1.59% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% 0.00% #DIV/0! 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0.00% 0.00% NR 0.00% 0.00%
WTP SSW INVENTORY Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
HEPA Filters Debris 4.62E-03 3.97E+00 4.72E-02 1.84E+01 2.34E-03 7.70E-08 1.24E-03 2.43E-01 1.54E-06 0.00E+00 6.52E+02 NR 0.00E+00 8.69E-02 6.64E-02 0.00E+00 1.67E+02 6.88E-08 1.09E-01 6.14E-03 1.09E-02 NR 1.86E+03 1.25E-06 7.72E-02 NR NR NR 7.53E+00 2.32E-06 0.00E+00 #DIV/0! 3.13E-05 5.97E-05 3.97E-08 6.04E-03 4.71E-04 1.35E-01 7.21E-02 NR NR NR 5.85E-03 0.00E+00 5.13E-01 5.54E-03 3.89E-06 2.05E-04 3.42E-05 NR 1.11E-04 1.18E-05 9.97E-07 NR 1.42E-01 1.95E-02
IX Resin Non-Debris 4.39E-02 1.42E+01 1.41E-01 1.59E-01 8.03E-03 4.95E-05 7.04E-03 1.12E-01 6.70E-04 4.26E+04 3.70E+01 NR 0.00E+00 4.63E+01 5.98E-07 7.19E-03 1.25E+02 4.54E-08 4.33E-05 1.03E-05 1.88E-08 NR 2.53E+03 1.36E-05 2.24E-01 NR NR NR 2.41E+00 1.89E-04 0.00E+00 #DIV/0! 8.08E-09 6.58E-04 6.01E-07 1.14E-08 6.30E-03 2.75E-01 2.07E-04 NR NR NR 8.39E-05 0.00E+00 2.84E-01 1.13E-03 1.29E-05 4.95E-12 5.70E-05 NR 1.37E-09 4.77E-06 4.12E-04 NR 1.27E-05 1.22E-04
LAW and HLW Carbon Beds Non-Debris 1.17E-12 2.66E-09 6.65E-11 1.37E-08 3.16E-13 1.17E-15 1.94E-13 3.63E-10 1.55E-14 2.33E-02 6.76E-10 NR 0.00E+00 5.39E+04 3.95E-11 3.22E+02 1.02E-07 1.52E-18 6.58E-11 3.69E-12 1.09E-11 NR 1.18E-06 3.22E-16 6.91E-11 NR NR NR 5.59E-09 4.51E-15 0.00E+00 #DIV/0! 4.34E-16 3.39E-14 3.16E-17 1.72E-11 5.68E-13 1.43E-10 4.33E-11 NR NR NR 1.04E-11 0.00E+00 3.17E-10 9.07E-12 1.06E-15 1.23E-13 1.59E-14 NR 1.55E-15 7.04E-15 9.77E-15 NR 8.49E-11 1.17E-11
Other Debris Debris 5.34E-02 4.67E+00 7.53E-02 1.11E+01 2.60E-02 3.13E-06 1.56E-02 1.23E-01 7.07E-05 1.94E+03 3.23E+00 NR 3.24E-03 2.87E+00 8.37E-02 6.45E-04 3.47E+00 7.61E-07 9.68E-03 2.74E-03 7.43E-02 NR 1.87E+02 1.50E-05 2.87E-01 NR NR NR 2.40E+00 3.45E-05 0.00E+00 #DIV/0! 3.56E-04 3.47E-04 1.46E-07 1.67E-03 1.92E-03 2.19E-02 1.02E-01 NR NR NR 3.06E-02 2.28E-07 1.34E-02 2.04E-02 3.38E-05 8.05E-05 5.72E-05 NR 1.26E-03 1.21E-05 2.56E-05 NR 2.04E-02 1.25E-02
HLW Silver Mordenite Absorbent Non-Debris 9.43E-14 8.77E-11 9.75E-11 1.58E-10 1.27E-13 1.57E-19 2.76E-14 5.55E-10 5.02E-17 1.21E-07 5.69E-10 NR 0.00E+00 8.72E+02 2.93E-13 2.54E-03 1.48E-09 9.50E-19 1.36E-13 2.39E-14 1.88E-11 NR 2.02E-09 1.79E-17 7.50E-11 NR NR NR 2.86E-09 5.94E-17 0.00E+00 #DIV/0! 8.67E-16 1.43E-15 3.64E-19 3.44E-11 5.62E-13 1.41E-10 1.78E-13 NR NR NR 2.08E-11 0.00E+00 2.67E-13 1.79E-11 7.50E-17 8.73E-16 1.85E-15 NR 3.11E-15 5.29E-17 2.95E-19 NR 1.51E-15 4.27E-14
SSW Total 1.02E-01 2.28E+01 2.64E-01 2.97E+01 3.63E-02 5.27E-05 2.39E-02 4.78E-01 7.43E-04 4.45E+04 6.92E+02 NR 3.24E-03 5.48E+04 1.50E-01 3.22E+02 2.96E+02 8.75E-07 1.19E-01 8.89E-03 8.52E-02 NR 4.57E+03 2.99E-05 5.88E-01 NR NR NR 1.23E+01 2.25E-04 0.00E+00 #DIV/0! 3.87E-04 1.06E-03 7.87E-07 7.70E-03 8.69E-03 4.32E-01 1.74E-01 NR NR NR 3.66E-02 2.28E-07 8.10E-01 2.71E-02 5.06E-05 2.85E-04 1.48E-04 NR 1.37E-03 2.87E-05 4.39E-04 NR 1.63E-01 3.22E-02
BBI 5.91E+05 1.99E+03 8.20E+04
Check 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% N/A 100% 100% 100% 100% 100% 100% 100% 100% 100% N/A 100% 100% 100% N/A N/A N/A 100% 100% 0% #DIV/0! 100% 100% 100% 100% 100% 100% 100% N/A N/A N/A 100% 100% 100% 100% 100% 100% 100% N/A 100% 100% 100% N/A 100% 100%
SE
CT
IO
N 1
SE
CT
IO
N 2
SE
CT
IO
N 3
AS
EC
TIO
N 4
SE
CT
IO
N 5
A
RPP-ENV-58562 Rev.03 5/9/2016 - 11:21 AM 107 of 118RPP-ENV-58562 Rev.03 9/26/2016 - 12:49 PM 107 of 124
RPP-ENV-58562, Rev. 3
A-19/A-20
Table A-9. Run Case 10B Radionuclides.
SVF-4097, IDF PA Case 10B - Recycle Pass Tc_Tc-99 Retention in ILAW Glass of 68% - Mass Balance, MMR-50054
WASTE STREAM 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
LAW Glass Subtotal (IDF) 1.17E+01 3.57E+03 3.10E+03 3.84E+02 5.70E+00 1.50E-01 7.73E+03 7.30E+03 0.00E+00 1.17E-01 4.63E-05 4.70E-04 6.01E-04 7.10E-03 1.32E+01 2.02E+02 2.25E-08 4.49E-08 5.12E-08 1.29E-01 8.31E+00 2.89E+00 1.18E-01 9.03E-02 1.70E+01 2.41E+02 2.63E+00 4.49E+03 9.56E+02 5.92E+03 7.48E+03 1.20E+02 7.53E-02 2.99E+00 1.32E+01 2.92E+02 0.00E+00 4.75E+01 9.70E-05 4.24E+03 1.08E+02 1.73E+05 1.73E+05 4.25E-04 2.98E-04 1.80E+04
LAW Spent Melter Subtotal (IDF) 1.23E-02 5.32E+00 2.70E+00 5.00E-01 7.31E-03 1.80E-04 9.81E+00 9.26E+00 0.00E+00 1.46E-04 5.78E-08 5.87E-07 7.51E-07 8.89E-06 1.88E-02 3.29E-01 2.81E-11 5.61E-11 6.40E-11 1.94E-04 1.39E-02 4.37E-03 1.78E-04 1.35E-04 2.15E-02 3.64E-01 3.97E-03 6.10E+00 1.29E+00 7.02E+00 1.00E+01 1.58E-01 9.90E-05 3.94E-03 1.77E-02 3.90E-01 0.00E+00 4.78E-02 1.21E-07 4.21E+00 1.38E-01 2.26E+02 2.26E+02 5.31E-07 3.72E-07 2.24E+01
ETF Solid Waste Form to IDF 2.30E-01 3.83E+01 1.01E+03 4.34E+00 1.87E+01 4.81E-02 2.48E+03 2.34E+03 2.40E+00 1.08E-03 4.21E-07 4.48E-06 5.55E-06 2.31E-03 1.52E-01 6.58E+01 2.04E-10 4.83E-10 4.65E-10 1.17E-03 7.55E-02 2.91E-02 1.19E-03 8.54E-04 1.54E-01 2.19E+00 2.66E-02 4.08E+01 8.68E+00 1.17E+02 6.80E+01 1.30E+00 8.62E-04 5.80E-02 1.43E-01 3.16E+00 3.91E+00 4.79E-01 8.65E-05 4.27E+01 3.53E+01 1.67E+03 1.67E+03 2.91E-07 5.66E-03 8.46E+03
Solid Waste Forms from Treatment Processes (IDF) 6.32E-05 7.18E-03 1.00E-02 1.68E-02 4.37E+00 7.48E-02 3.65E+03 3.44E+03 0.00E+00 2.71E-03 6.81E-07 4.12E-05 2.04E-05 2.70E-08 1.40E-06 7.69E-04 1.19E-09 4.01E-09 5.54E-09 2.07E-08 1.43E-06 4.86E-07 1.99E-08 1.47E-08 1.89E-06 9.61E-03 4.41E-07 1.75E-02 1.71E-02 9.34E-03 8.61E-04 3.46E-04 8.63E-09 7.66E-07 5.76E-04 9.20E-04 0.00E+00 4.09E-04 1.71E-05 3.66E-02 4.16E-03 2.62E+01 2.62E+01 2.75E-04 -9.62E-04 1.12E+01
Non-IDF Stream 2.76E-03 2.14E+02 8.23E-02 1.37E-01 4.89E-01 7.11E+02 3.88E+07 3.66E+07 8.25E+02 3.23E+06 8.12E+02 4.91E+04 2.44E+04 5.44E-06 -8.64E+00 -2.55E+02 1.42E+00 4.79E+00 6.61E+00 8.21E+00 6.39E+02 2.14E+02 8.72E+00 6.05E+00 9.09E+01 2.26E+03 1.94E+02 4.34E+04 9.18E+03 1.43E+05 7.20E+04 7.46E-02 6.83E-01 6.46E+01 5.12E-03 1.11E-01 2.80E+03 1.42E+03 3.77E+03 1.27E+05 -2.95E-02 4.36E+07 4.36E+07 3.46E+03 2.93E+03 6.30E+00
BBI 1.20E+01 3.89E+03 4.13E+03 3.91E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 5.51E+02 3.57E+06 9.07E+02 5.30E+04 2.55E+04 9.95E-03 4.14E+00 6.77E+00 1.48E+00 5.16E+00 6.77E+00 8.87E+00 6.82E+02 2.37E+02 9.71E+00 6.50E+00 1.15E+02 2.63E+03 2.15E+02 4.94E+04 1.08E+04 1.57E+05 8.38E+04 1.22E+02 8.26E-01 7.23E+01 1.35E+01 2.98E+02 2.82E+03 1.62E+03 4.10E+03 1.44E+05 1.44E+02 4.76E+07 4.76E+07 3.73E+03 3.17E+03 2.65E+04
HTWOS Feed 1.20E+01 3.89E+03 4.13E+03 3.91E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 8.28E+02 3.57E+06 9.07E+02 5.30E+04 2.55E+04 9.95E-03 4.14E+00 6.77E+00 1.48E+00 5.16E+00 6.77E+00 8.87E+00 6.82E+02 2.37E+02 9.71E+00 6.50E+00 1.15E+02 2.64E+03 2.16E+02 5.14E+04 1.09E+04 1.57E+05 8.39E+04 1.22E+02 8.27E-01 7.23E+01 1.35E+01 2.98E+02 2.82E+03 1.62E+03 4.10E+03 1.44E+05 1.44E+02 4.76E+07 4.76E+07 3.73E+03 3.17E+03 2.65E+04
HTWOS Feed Adjusted Minus TF and TRU Accumulation 1.20E+01 3.83E+03 4.11E+03 3.90E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 8.27E+02 3.27E+06 8.26E+02 4.95E+04 2.45E+04 9.43E-03 4.53E+00 9.30E+00 1.43E+00 4.84E+00 6.63E+00 8.39E+00 6.51E+02 2.19E+02 8.95E+00 6.20E+00 1.08E+02 2.52E+03 1.99E+02 4.83E+04 1.02E+04 1.50E+05 8.00E+04 1.21E+02 7.64E-01 6.80E+01 1.34E+01 2.96E+02 2.81E+03 1.48E+03 3.80E+03 1.33E+05 1.44E+02 4.40E+07 4.40E+07 3.49E+03 2.96E+03 2.65E+04
ACCUMULATION STREAM 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
PT-Accumulation 6.06E-04 1.55E+00 2.22E-01 4.26E-02 2.17E-02 1.90E+00 2.13E+05 2.01E+05 1.40E-01 3.81E+04 1.23E+01 3.96E+02 1.15E+02 1.34E-06 -1.48E-01 -5.15E+00 5.48E-03 4.77E-02 2.24E-02 5.19E-02 3.37E+00 2.28E+00 9.71E-02 5.07E-02 3.51E-01 1.04E+01 2.18E+00 2.97E+02 6.05E+01 5.49E+02 3.65E+02 5.60E-03 3.89E-03 2.79E-01 6.81E-04 1.49E-02 2.84E+00 1.46E+01 2.86E+01 1.32E+03 1.80E-02 2.00E+05 2.00E+05 2.94E+01 2.80E+01 2.64E+00
TF-Accumulation 1.28E-05 6.61E+01 2.11E+01 1.96E+00 7.54E-02 2.40E-02 1.64E+04 1.54E+04 2.12E-01 3.01E+05 8.12E+01 3.48E+03 1.05E+03 5.20E-04 -3.91E-01 -2.53E+00 4.70E-02 3.25E-01 1.34E-01 4.77E-01 3.06E+01 1.78E+01 7.63E-01 3.01E-01 6.37E+00 1.21E+02 1.72E+01 3.15E+03 6.67E+02 6.58E+03 3.89E+03 8.66E-01 6.37E-02 4.30E+00 1.34E-01 2.43E+00 3.58E+00 1.37E+02 3.02E+02 1.17E+04 4.57E-02 3.60E+06 3.60E+06 2.47E+02 2.13E+02 8.04E+00
TRU-Accumulation 3.92E-14 5.50E-04 3.41E-06 6.30E-05 6.28E-06 1.86E-09 2.64E+00 2.50E+00 8.33E-04 1.13E+00 3.05E-05 1.77E-02 7.06E-03 7.63E-08 1.47E-06 4.74E-12 2.31E-10 4.67E-06 1.94E-12 6.29E-08 5.45E-09 7.26E-03 2.34E-04 7.01E-05 2.54E-05 2.82E-02 5.37E-03 2.23E+00 2.70E-01 3.27E-01 7.48E-01 5.56E-05 1.33E-05 3.19E-05 5.76E-07 1.22E-05 3.85E-03 1.44E-04 5.41E-04 1.94E-02 3.44E-05 3.34E+01 3.34E+01 1.89E-02 1.73E-02 1.18E-02
LAW Accumulation 1.51E-04 3.73E-01 6.10E-02 9.54E-03 1.02E-03 2.61E-06 2.03E-01 1.91E-01 1.94E-02 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.48E-07 3.41E-03 1.50E-01 0.00E+00 0.00E+00 0.00E+00 6.97E-06 4.65E-04 3.40E-04 1.46E-05 7.97E-06 3.74E-04 1.02E-02 3.24E-04 2.81E-01 5.58E-02 5.19E-02 3.95E-01 1.36E-03 3.68E-06 2.39E-05 1.64E-04 3.60E-03 6.06E-02 6.03E-03 0.00E+00 5.49E-01 4.61E-03 3.56E+00 3.56E+00 0.00E+00 0.00E+00 7.40E-01
HLW-Accumulation 6.73E-08 2.11E-03 1.04E-04 2.19E-05 4.52E-04 1.38E-02 1.90E+03 1.79E+03 2.29E-05 2.46E+03 8.15E-01 2.57E+01 7.42E+00 6.25E-10 -7.99E-03 -3.34E-01 3.17E-04 2.38E-03 1.25E-03 2.91E-03 1.87E-01 1.23E-01 5.22E-03 2.68E-03 2.13E-02 6.32E-01 1.17E-01 1.82E+01 3.71E+00 3.56E+01 2.17E+01 5.96E-06 2.38E-04 1.83E-02 4.32E-07 9.44E-06 1.52E+00 6.85E-01 1.76E+00 6.18E+01 7.26E-06 1.07E+04 1.07E+04 1.84E+00 1.63E+00 2.66E-04
SLAW-Accumulation 1.49E-04 3.29E-01 6.38E-02 9.61E-03 1.17E-03 3.07E-06 2.60E-01 2.45E-01 1.93E-02 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.72E-07 3.17E-03 1.50E-01 0.00E+00 0.00E+00 0.00E+00 5.53E-06 3.67E-04 2.67E-04 1.14E-05 6.17E-06 4.09E-04 8.91E-03 2.55E-04 2.48E-01 4.92E-02 6.34E-02 3.39E-01 1.51E-03 3.22E-06 2.81E-05 1.68E-04 3.68E-03 7.55E-02 5.53E-03 0.00E+00 5.04E-01 5.31E-03 9.09E+00 9.09E+00 0.00E+00 0.00E+00 1.00E+00
LAWPS-Accumulation 4.00E-06 2.51E-03 1.45E-03 5.68E-04 2.69E-05 4.84E-04 4.35E+01 4.11E+01 1.94E-03 0.00E+00 0.00E+00 0.00E+00 0.00E+00 6.94E-09 5.37E-06 1.23E-05 0.00E+00 0.00E+00 0.00E+00 3.94E-08 2.22E-06 1.40E-06 5.81E-08 4.46E-08 2.10E-05 1.84E-04 1.31E-06 4.13E-03 9.53E-04 7.79E-03 6.20E-03 7.07E-05 8.32E-08 3.48E-06 5.09E-06 1.12E-04 8.47E-04 1.18E-05 0.00E+00 1.05E-03 1.25E-04 1.98E-01 1.98E-01 0.00E+00 0.00E+00 2.98E-02
ETF-Accumulation 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00
LERF-Accumulation 1.20E-04 2.67E-01 6.89E-01 7.69E-03 3.50E-02 3.05E-05 3.30E+00 3.12E+00 7.34E-03 4.20E-18 1.66E-21 1.69E-20 2.16E-20 4.60E-06 1.55E-03 1.37E+00 8.09E-25 1.62E-24 1.84E-24 3.52E-06 2.24E-04 1.29E-04 5.47E-06 2.88E-06 3.25E-04 4.23E-03 1.23E-04 1.09E-01 2.26E-02 1.41E-01 1.39E-01 1.99E-03 2.42E-06 6.54E-05 1.52E-04 3.32E-03 3.91E+00 2.56E-03 3.49E-21 2.29E-01 6.13E-02 1.50E+01 1.50E+01 3.45E-22 6.58E-20 1.45E+01
Total Accumulation 1.04E-03 6.87E+01 2.21E+01 2.03E+00 1.35E-01 1.94E+00 2.31E+05 2.18E+05 4.01E-01 3.41E+05 9.43E+01 3.91E+03 1.17E+03 5.27E-04 -5.39E-01 -6.34E+00 5.28E-02 3.75E-01 1.57E-01 5.32E-01 3.41E+01 2.02E+01 8.66E-01 3.54E-01 6.74E+00 1.32E+02 1.95E+01 3.47E+03 7.32E+02 7.17E+03 4.28E+03 8.77E-01 6.78E-02 4.60E+00 1.35E-01 2.45E+00 1.20E+01 1.52E+02 3.32E+02 1.31E+04 1.35E-01 3.81E+06 3.81E+06 2.78E+02 2.43E+02 2.70E+01
Accumulation minus TF and TRU 1.03E-03 2.52E+00 1.04E+00 7.00E-02 5.93E-02 1.92E+00 2.15E+05 2.03E+05 1.88E-01 4.05E+04 1.31E+01 4.21E+02 1.23E+02 6.67E-06 -1.48E-01 -3.81E+00 5.80E-03 5.00E-02 2.36E-02 5.48E-02 3.56E+00 2.40E+00 1.02E-01 5.34E-02 3.73E-01 1.11E+01 2.30E+00 3.16E+02 6.43E+01 5.85E+02 3.87E+02 1.05E-02 4.14E-03 2.97E-01 1.17E-03 2.56E-02 8.41E+00 1.53E+01 3.04E+01 1.38E+03 8.94E-02 2.11E+05 2.11E+05 3.12E+01 2.96E+01 1.89E+01
ADJUSTED INVENTORY TO INCLUDE ACCUMULATION-Radionuclides decayed to 1/1/2008 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
LAW Glass Subtotal (IDF) 1.17E+01 3.57E+03 3.10E+03 3.85E+02 5.72E+00 1.50E-01 7.77E+03 7.34E+03 0.00E+00 1.18E-01 4.70E-05 4.74E-04 6.04E-04 7.10E-03 1.27E+01 1.19E+02 2.26E-08 4.54E-08 5.14E-08 1.30E-01 8.35E+00 2.92E+00 1.20E-01 9.11E-02 1.70E+01 2.43E+02 2.66E+00 4.52E+03 9.62E+02 5.95E+03 7.52E+03 1.20E+02 7.57E-02 3.01E+00 1.32E+01 2.92E+02 0.00E+00 4.80E+01 9.77E-05 4.28E+03 1.08E+02 1.74E+05 1.74E+05 4.29E-04 3.01E-04 1.80E+04
LAW Spent Melter Subtotal (IDF) 1.23E-02 5.32E+00 2.70E+00 5.00E-01 7.33E-03 1.81E-04 9.86E+00 9.31E+00 0.00E+00 1.48E-04 5.88E-08 5.92E-07 7.55E-07 8.90E-06 1.82E-02 1.94E-01 2.82E-11 5.67E-11 6.42E-11 1.95E-04 1.40E-02 4.42E-03 1.80E-04 1.36E-04 2.15E-02 3.66E-01 4.02E-03 6.14E+00 1.30E+00 7.05E+00 1.01E+01 1.58E-01 9.96E-05 3.96E-03 1.77E-02 3.90E-01 0.00E+00 4.83E-02 1.22E-07 4.26E+00 1.38E-01 2.27E+02 2.27E+02 5.36E-07 3.76E-07 2.24E+01
ETF Solid Waste Form to IDF 2.30E-01 3.83E+01 1.01E+03 4.34E+00 1.88E+01 4.83E-02 2.49E+03 2.35E+03 2.40E+00 1.09E-03 4.28E-07 4.52E-06 5.57E-06 2.31E-03 1.47E-01 3.88E+01 2.05E-10 4.88E-10 4.67E-10 1.18E-03 7.59E-02 2.95E-02 1.21E-03 8.61E-04 1.55E-01 2.20E+00 2.69E-02 4.11E+01 8.74E+00 1.17E+02 6.83E+01 1.30E+00 8.67E-04 5.83E-02 1.43E-01 3.16E+00 3.92E+00 4.84E-01 8.71E-05 4.32E+01 3.53E+01 1.68E+03 1.68E+03 2.93E-07 5.71E-03 8.47E+03
Solid Waste Forms from Treatment Processes (IDF) 6.32E-05 7.19E-03 1.00E-02 1.68E-02 4.38E+00 7.50E-02 3.67E+03 3.46E+03 0.00E+00 2.74E-03 6.92E-07 4.15E-05 2.05E-05 2.70E-08 1.35E-06 4.54E-04 1.20E-09 4.05E-09 5.56E-09 2.08E-08 1.43E-06 4.92E-07 2.01E-08 1.48E-08 1.90E-06 9.66E-03 4.46E-07 1.76E-02 1.72E-02 9.38E-03 8.65E-04 3.46E-04 8.67E-09 7.70E-07 5.76E-04 9.20E-04 0.00E+00 4.13E-04 1.72E-05 3.70E-02 4.17E-03 2.64E+01 2.64E+01 2.77E-04 -9.71E-04 1.12E+01
Non-IDF Stream 2.76E-03 2.15E+02 8.24E-02 1.37E-01 4.90E-01 7.13E+02 3.90E+07 3.68E+07 8.25E+02 3.27E+06 8.25E+02 4.95E+04 2.45E+04 5.44E-06 -8.36E+00 -1.51E+02 1.43E+00 4.84E+00 6.63E+00 8.26E+00 6.43E+02 2.16E+02 8.82E+00 6.10E+00 9.12E+01 2.27E+03 1.96E+02 4.37E+04 9.24E+03 1.44E+05 7.24E+04 7.46E-02 6.87E-01 6.49E+01 5.12E-03 1.11E-01 2.81E+03 1.43E+03 3.80E+03 1.28E+05 -2.95E-02 4.38E+07 4.38E+07 3.49E+03 2.96E+03 6.30E+00
1.20E+01 3.83E+03 4.11E+03 3.90E+02 2.94E+01 7.13E+02 3.90E+07 3.68E+07 8.27E+02 3.27E+06 8.25E+02 4.95E+04 2.45E+04 9.43E-03 4.53E+00 7.74E+00 1.43E+00 4.84E+00 6.63E+00 8.39E+00 6.51E+02 2.19E+02 8.94E+00 6.20E+00 1.08E+02 2.52E+03 1.99E+02 4.83E+04 1.02E+04 1.50E+05 8.00E+04 1.21E+02 7.64E-01 6.80E+01 1.34E+01 2.96E+02 2.81E+03 1.48E+03 3.80E+03 1.33E+05 1.44E+02 4.40E+07 4.40E+07 3.49E+03 2.96E+03 2.65E+04
100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 120% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100%
ADJUSTED INVENTORY TO INCLUDE ACCUMULATION-Radionuclides decayed to 1/1/2051 IDF Waste Streams Only 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
LAW Glass Subtotal (IDF) 2.39E-12 4.31E+02 6.28E-02 3.84E+02 5.72E+00 8.11E-08 2.89E+03 2.72E+03 0.00E+00 8.50E-02 5.20E-06 1.48E-05 1.14E-06 6.97E-03 3.24E+00 6.75E-01 2.25E-08 4.53E-08 5.14E-08 8.49E-02 8.35E+00 2.92E+00 1.20E-01 9.11E-02 1.70E+01 1.73E+02 2.66E+00 4.52E+03 9.57E+02 5.76E+03 9.49E+02 9.69E+01 7.57E-02 2.99E+00 4.75E+00 5.63E+01 0.00E+00 4.79E+01 3.42E-07 3.19E+03 1.08E+02 6.16E+04 6.16E+04 4.29E-04 4.09E-04 1.80E+04
LAW Spent Melter Subtotal (IDF) 2.51E-15 6.43E-01 5.47E-05 5.00E-01 7.33E-03 9.75E-11 3.66E+00 3.46E+00 0.00E+00 1.06E-04 6.50E-09 1.85E-08 1.42E-09 8.73E-06 4.62E-03 1.10E-03 2.81E-11 5.67E-11 6.42E-11 1.28E-04 1.40E-02 4.42E-03 1.80E-04 1.36E-04 2.15E-02 2.60E-01 4.02E-03 6.13E+00 1.29E+00 6.86E+00 1.27E+00 1.28E-01 9.96E-05 3.94E-03 6.37E-03 7.52E-02 0.00E+00 4.83E-02 4.28E-10 3.17E+00 1.38E-01 8.05E+01 8.05E+01 5.36E-07 5.11E-07 2.24E+01
ETF Solid Waste Form to IDF 4.70E-14 4.62E+00 2.04E-02 4.34E+00 1.88E+01 2.60E-08 9.25E+02 8.73E+02 2.39E+00 7.84E-04 4.74E-08 1.41E-07 1.05E-08 2.27E-03 3.75E-02 2.20E-01 2.04E-10 4.87E-10 4.67E-10 7.71E-04 7.59E-02 2.95E-02 1.21E-03 8.61E-04 1.55E-01 1.57E+00 2.69E-02 4.10E+01 8.70E+00 1.11E+02 8.62E+00 1.05E+00 8.67E-04 5.80E-02 5.14E-02 6.09E-01 3.49E-01 4.84E-01 3.05E-07 3.22E+01 3.53E+01 5.97E+02 5.97E+02 2.93E-07 8.97E-04 8.46E+03
Solid Waste Forms from Treatment Processes (IDF) 1.29E-17 8.68E-04 2.03E-07 1.68E-02 4.38E+00 4.04E-08 1.36E+03 1.28E+03 0.00E+00 1.97E-03 7.66E-08 1.29E-06 3.87E-08 2.65E-08 3.48E-07 2.58E-06 1.19E-09 4.05E-09 5.56E-09 1.36E-08 1.43E-06 4.92E-07 2.01E-08 1.48E-08 1.90E-06 6.87E-03 4.46E-07 1.76E-02 1.72E-02 8.78E-03 1.09E-04 2.80E-04 8.67E-09 7.67E-07 2.07E-04 1.77E-04 0.00E+00 4.13E-04 6.02E-08 2.75E-02 4.17E-03 9.36E+00 9.36E+00 2.77E-04 8.13E-05 1.12E+01
SSW FRACTIONS BASED ON 10-010 and 10-009 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
HEPA fraction NR NR NR 51.81% 1.03% 52.45% 50.81% NR 10.40% NR 65.24% 64.99% 65.27% NR NR NR NR NR NR NR 68.98% 68.94% 68.90% 68.85% 54.86% 68.68% 68.39% 68.53% 68.48% 70.74% 68.04% NR NR NR NR NR 0.01% 56.98% 62.75% 57.75% 71.82% 65.75% NR NR NR 87.60%
IX Resin fraction NR NR NR 43.80% 0.14% 8.96% 9.27% NR 1.53% NR 7.64% 7.67% 7.61% NR NR NR NR NR NR NR 0.00% 0.00% 0.00% 0.00% 42.37% 0.00% 0.00% 0.00% 0.00% 3.83% 0.00% NR NR NR NR NR 49.09% 20.28% 19.08% 19.89% 26.01% 0.09% NR NR NR 11.86%
LAW and HLW Carbon Bed fraction NR NR NR 0.00% 36.47% 0.00% 0.00% NR 34.07% NR 0.00% 0.00% 0.00% NR NR NR NR NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR NR NR 36.25% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00%
Other Debris fraction NR NR NR 4.39% 0.01% 38.59% 39.92% NR 24.63% NR 27.13% 27.34% 27.12% NR NR NR NR NR NR NR 31.02% 31.06% 31.10% 31.15% 2.77% 31.32% 31.61% 31.47% 31.52% 25.43% 31.96% NR NR NR NR NR 14.62% 22.75% 18.17% 22.35% 2.17% 34.16% NR NR NR 0.54%
HLW Silver Mordenite Absorbent fraction NR NR NR 0.00% 62.35% 0.00% 0.00% NR 29.36% NR 0.00% 0.00% 0.00% NR NR NR NR NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR NR NR 0.03% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00%
WTP SSW INVENTORY-Radionuclides decayed to 1/1/2008 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
HEPA Filters Debris NR NR NR 8.73E-03 4.52E-02 3.93E-02 1.86E+03 NR 0.00E+00 NR 4.52E-07 2.70E-05 1.34E-05 NR NR NR NR NR NR NR 9.89E-07 3.39E-07 1.38E-08 1.02E-08 1.04E-06 6.63E-03 3.05E-07 1.21E-02 1.18E-02 6.63E-03 5.89E-04 NR NR NR NR NR 0.00E+00 2.35E-04 1.08E-05 2.13E-02 2.99E-03 1.73E+01 NR NR NR 9.80E+00
IX Resin Non-Debris NR NR NR 7.38E-03 6.00E-03 6.72E-03 3.40E+02 NR 0.00E+00 NR 5.29E-08 3.18E-06 1.56E-06 NR NR NR NR NR NR NR 4.81E-13 1.69E-13 5.89E-15 6.96E-15 8.04E-07 6.99E-08 1.56E-13 1.28E-07 1.26E-07 3.59E-04 6.40E-09 NR NR NR NR NR 0.00E+00 8.38E-05 3.28E-06 7.35E-03 1.08E-03 2.47E-02 NR NR NR 1.33E+00
LAW and HLW Carbon Beds Non-Debris NR NR NR 1.75E-13 1.60E+00 1.40E-11 5.78E-07 NR 0.00E+00 NR 1.43E-18 8.94E-17 4.37E-17 NR NR NR NR NR NR NR 5.36E-19 2.03E-19 8.58E-21 7.90E-21 1.91E-17 3.72E-15 1.87E-19 6.83E-15 6.66E-15 1.25E-14 3.39E-16 NR NR NR NR NR 0.00E+00 1.72E-14 1.11E-16 1.53E-12 3.03E-13 3.06E-09 NR NR NR 1.48E-09
Other Debris Debris NR NR NR 7.39E-04 3.96E-04 2.90E-02 1.46E+03 NR 0.00E+00 NR 1.88E-07 1.14E-05 5.57E-06 NR NR NR NR NR NR NR 4.45E-07 1.53E-07 6.25E-09 4.62E-09 5.25E-08 3.02E-03 1.41E-07 5.54E-03 5.43E-03 2.39E-03 2.76E-04 NR NR NR NR NR 0.00E+00 9.40E-05 3.12E-06 8.26E-03 9.05E-05 9.00E+00 NR NR NR 6.02E-02
HLW Silver Mordenite Absorbent Non-Debris NR NR NR 1.69E-16 2.73E+00 2.78E-11 1.15E-06 NR 0.00E+00 NR 3.60E-19 2.75E-17 1.32E-17 NR NR NR NR NR NR NR 1.07E-18 4.07E-19 1.72E-20 1.58E-20 1.24E-20 7.43E-15 3.75E-19 1.37E-14 1.33E-14 7.36E-15 6.78E-16 NR NR NR NR NR 0.00E+00 2.77E-14 2.38E-17 2.47E-12 3.72E-14 6.11E-09 NR NR NR 1.24E-12
SSW Total NR NR NR 1.68E-02 4.38E+00 7.50E-02 3.67E+03 NR 0.00E+00 NR 6.92E-07 4.15E-05 2.05E-05 NR NR NR NR NR NR NR 1.43E-06 4.92E-07 2.01E-08 1.48E-08 1.90E-06 9.66E-03 4.46E-07 1.76E-02 1.72E-02 9.38E-03 8.65E-04 NR NR NR NR NR 0.00E+00 4.13E-04 1.72E-05 3.70E-02 4.17E-03 2.64E+01 NR NR NR 1.12E+01
BBI 2.94E+01 3.90E+07 4.76E+07 2.65E+04
Check N/A N/A N/A 100% 100% 100% 100% N/A #DIV/0! N/A 100% 100% 100% N/A N/A N/A N/A N/A N/A N/A 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% N/A N/A N/A N/A N/A #DIV/0! 100% 100% 100% 100% 100% N/A N/A N/A 100%
WTP SSW INVENTORY-Radionuclides decayed to 1/1/2051 106-Ru 113m-Cd 125-Sb 126-Sn 129-I 134-Cs 137-Cs 137m-Ba 14-C 151-Sm 152-Eu 154-Eu 155-Eu 226-Ra 227-Ac 228-Ra 229-Th 231-Pa 232-Th 232-U 233-U 234-U 235-U 236-U 237-Np 238-Pu 238-U 239-Pu 240-Pu 241-Am 241-Pu 242-Cm 242-Pu 243-Am 243-Cm 244-Cm 3-H 59-Ni 60-Co 63-Ni 79-Se 90-Sr 90-Y 93-Zr 93m-Nb 99-Tc
HEPA Filters Debris NR NR NR 8.73E-03 4.52E-02 2.12E-08 6.91E+02 NR 0.00E+00 NR 5.00E-08 8.41E-07 2.52E-08 NR NR NR NR NR NR NR 9.88E-07 3.39E-07 1.38E-08 1.02E-08 1.04E-06 4.72E-03 3.05E-07 1.21E-02 1.18E-02 6.21E-03 7.43E-05 NR NR NR NR NR 0.00E+00 2.35E-04 3.78E-08 1.59E-02 2.99E-03 6.15E+00 NR NR NR 9.79E+00
IX Resin Non-Debris NR NR NR 7.38E-03 6.00E-03 3.62E-09 1.26E+02 NR 0.00E+00 NR 5.85E-09 9.92E-08 2.94E-09 NR NR NR NR NR NR NR 4.81E-13 1.69E-13 5.89E-15 6.96E-15 8.04E-07 4.97E-08 1.56E-13 1.28E-07 1.25E-07 3.35E-04 8.08E-10 NR NR NR NR NR 0.00E+00 8.37E-05 1.15E-08 5.47E-03 1.08E-03 8.77E-03 NR NR NR 1.33E+00
LAW and HLW Carbon Beds Non-Debris NR NR NR 1.75E-13 1.60E+00 7.54E-18 2.15E-07 NR 0.00E+00 NR 1.58E-19 2.78E-18 8.23E-20 NR NR NR NR NR NR NR 5.36E-19 2.03E-19 8.58E-21 7.90E-21 1.91E-17 2.65E-15 1.87E-19 6.82E-15 6.63E-15 1.17E-14 4.28E-17 NR NR NR NR NR 0.00E+00 1.72E-14 3.90E-19 1.14E-12 3.03E-13 1.09E-09 NR NR NR 1.48E-09
Other Debris Debris NR NR NR 7.39E-04 3.96E-04 1.56E-08 5.43E+02 NR 0.00E+00 NR 2.08E-08 3.54E-07 1.05E-08 NR NR NR NR NR NR NR 4.45E-07 1.53E-07 6.25E-09 4.62E-09 5.25E-08 2.15E-03 1.41E-07 5.54E-03 5.41E-03 2.23E-03 3.49E-05 NR NR NR NR NR 0.00E+00 9.39E-05 1.09E-08 6.15E-03 9.05E-05 3.20E+00 NR NR NR 6.02E-02
HLW Silver Mordenite Absorbent Non-Debris NR NR NR 1.69E-16 2.73E+00 1.50E-17 4.26E-07 NR 0.00E+00 NR 3.98E-20 8.56E-19 2.48E-20 NR NR NR NR NR NR NR 1.07E-18 4.06E-19 1.72E-20 1.58E-20 1.24E-20 5.29E-15 3.75E-19 1.36E-14 1.33E-14 6.89E-15 8.56E-17 NR NR NR NR NR 0.00E+00 2.77E-14 8.33E-20 1.84E-12 3.72E-14 2.17E-09 NR NR NR 1.24E-12SE
CT
ION
5B
SE
CT
ION
1S
EC
TIO
N 2
SE
CT
ION
3A
SE
CT
ION
4S
EC
TIO
N 5
AS
EC
TIO
N 3
B
RPP-ENV-58562 Rev.03 5/9/2016 - 11:21 AM 108 of 118RPP-ENV-58562 Rev.03 9/26/2016 - 12:49 PM 108 of 124
RPP-ENV-58562, Rev. 3
A-21/A-22
Table A-10. Run Case 10B Chemicals.
SVF-4097, IDF PA Case 10B - Recycle Pass Tc_Tc-99 Retention in ILAW Glass of 68% - Mass Balance, MMR-50054
WASTE STREAM Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
LAW Glass Subtotal (IDF) 1.22E+03 1.95E+07 3.60E+03 1.83E+07 1.04E+01 4.92E+02 6.22E+04 6.99E+03 5.12E+04 4.09E+05 4.60E+05 4.56E-01 3.28E+02 5.81E+05 2.33E+07 0.00E+00 8.92E+05 3.72E-05 2.91E+06 5.39E+06 3.80E-05 6.38E+03 7.73E+07 3.26E+03 2.30E+03 0.00E+00 0.00E+00 0.00E+00 7.16E+04 2.11E+03 0.00E+00 0.00E+00 7.67E+01 2.69E+02 0.00E+00 3.05E+03 2.68E+03 3.88E+03 1.28E+08 0.00E+00 2.38E+06 0.00E+00 8.72E+01 6.61E-02 1.06E+03 1.56E+03 4.65E-04 7.21E+06 1.06E-04 0.00E+00 7.88E+03 7.24E-01 4.11E+03 9.07E+01 1.43E+07 1.33E+07
LAW Spent Melter Subtotal (IDF) 1.67E+00 2.65E+04 4.26E+00 2.50E+04 1.95E-02 6.45E-01 8.69E+01 1.02E+01 7.60E+01 5.20E+02 6.39E+02 5.84E-04 3.64E-01 7.64E+02 3.18E+04 0.00E+00 1.06E+03 4.65E-08 4.14E+03 7.35E+03 4.75E-08 8.49E+00 1.05E+05 4.48E+00 3.03E+00 0.00E+00 0.00E+00 0.00E+00 9.55E+01 1.58E+00 0.00E+00 0.00E+00 1.04E-01 2.35E-01 0.00E+00 2.72E+00 3.34E+00 4.36E+00 1.75E+05 0.00E+00 3.29E+03 0.00E+00 5.17E-02 1.14E-04 1.32E+00 2.13E+00 5.81E-07 9.84E+03 1.32E-07 2.44E-02 1.19E+01 1.06E-03 2.22E+00 1.25E-01 1.95E+04 1.82E+04
ETF Solid Waste Form to IDF 2.46E+01 1.14E+04 1.17E+03 1.62E+02 7.87E-01 5.64E+00 1.35E+03 6.33E+01 1.32E+03 3.69E+05 3.45E+04 8.90E-02 3.37E+01 6.06E+05 3.22E+02 1.64E+03 4.66E+04 2.73E-03 2.41E+01 1.14E+00 3.38E+01 1.38E+02 1.76E+06 3.42E+01 2.36E+01 2.17E+04 2.23E+06 8.73E+04 7.17E+03 2.18E+01 5.50E+04 0.00E+00 6.97E-01 5.58E+00 0.00E+00 3.09E+01 8.75E+02 1.26E+03 1.41E+03 0.00E+00 0.00E+00 9.26E+05 1.14E+01 1.02E-03 4.99E+02 5.15E+02 4.22E-06 1.08E-05 4.87E-05 5.16E+03 7.98E+01 1.45E-04 2.09E-02 7.96E-03 3.17E+01 1.42E-05
Solid Waste Forms from Treatment Processes (IDF) 9.48E-02 2.28E+01 2.51E-01 2.97E+01 3.50E-02 5.27E-05 2.42E-02 4.63E-01 7.51E-04 4.45E+04 6.92E+02 1.94E-01 3.19E-03 5.47E+04 1.48E-01 3.22E+02 2.96E+02 8.74E-07 1.19E-01 8.84E-03 8.45E-02 1.42E-02 4.55E+03 3.00E-05 5.49E-01 0.00E+00 0.00E+00 0.00E+00 1.24E+01 2.25E-04 3.99E+03 6.86E-07 3.58E-04 1.06E-03 7.85E-07 7.70E-03 8.68E-03 4.15E-01 1.68E-01 3.79E+03 0.00E+00 0.00E+00 3.49E-02 2.27E-07 6.59E-01 2.56E-02 5.04E-05 2.85E-04 1.43E-04 0.00E+00 1.32E-03 2.84E-05 4.39E-04 2.63E-06 1.63E-01 3.21E-02
Non-IDF Stream 2.50E+03 2.47E+06 8.52E+01 1.49E+06 8.56E+03 2.71E+00 4.77E+05 1.61E+03 6.61E+03 4.50E+03 6.56E+04 2.07E+03 2.33E+03 3.02E+04 1.53E+06 -2.70E+00 1.64E+04 4.21E+04 7.51E+05 2.28E+04 4.63E+05 2.24E+01 2.04E+06 5.87E+03 1.16E+05 1.68E+07 5.75E+07 2.53E+07 2.64E+03 5.16E-01 5.07E+06 8.18E+02 7.41E+02 8.53E-02 9.37E+02 5.12E-01 1.55E+02 3.08E+01 5.57E+06 -3.79E+03 -2.39E+06 2.88E+06 5.97E+04 2.62E+02 3.72E-01 8.35E+02 6.01E+04 1.38E+03 6.55E+03 8.65E+05 5.81E+05 2.38E+03 4.40E+01 4.78E+02 4.31E+02 4.04E+05
BBI 4.03E+03 8.67E+06 4.88E+03 1.52E+04 9.42E+03 5.02E+02 5.61E+05 8.87E+03 6.96E+03 8.27E+05 5.91E+05 2.09E+03 2.91E+03 1.28E+06 1.27E+06 1.99E+03 9.57E+05 3.20E+04 1.94E+03 2.19E+04 1.64E+05 6.56E+03 4.92E+07 9.70E+03 9.87E+04 1.19E+07 5.60E+07 4.45E+06 8.20E+04 2.14E+03 5.18E+06 8.43E+02 8.45E+02 2.78E+02 9.47E+02 3.09E+03 3.73E+03 5.18E+03 8.41E+05 0.00E+00 0.00E+00 3.82E+06 4.23E+04 2.72E+02 1.56E+03 2.92E+03 6.15E+04 1.51E+03 6.98E+03 8.71E+05 6.45E+05 2.58E+03 4.16E+03 5.81E+02 6.08E+03 4.09E+05
HTWOS Feed 4.03E+03 2.25E+07 4.88E+03 1.99E+07 9.42E+03 5.02E+02 6.02E+05 8.87E+03 6.00E+04 8.28E+05 5.91E+05 2.09E+03 2.91E+03 1.28E+06 2.50E+07 1.99E+03 9.57E+05 4.47E+04 3.67E+06 5.42E+06 4.79E+05 6.56E+03 8.13E+07 9.70E+03 1.25E+05 1.68E+07 5.98E+07 2.54E+07 8.20E+04 2.14E+03 5.20E+06 8.43E+02 8.77E+02 2.78E+02 9.47E+02 3.09E+03 3.73E+03 5.18E+03 1.34E+08 0.00E+00 0.00E+00 3.83E+06 6.36E+04 2.72E+02 1.56E+03 2.92E+03 6.15E+04 7.22E+06 6.98E+03 8.71E+05 6.47E+05 2.58E+03 4.16E+03 5.81E+02 1.43E+07 1.38E+07
HTWOS Feed Adjusted Minus TF and TRU Accumulation 3.82E+03 2.20E+07 4.87E+03 1.99E+07 8.70E+03 5.02E+02 5.46E+05 8.67E+03 5.96E+04 8.28E+05 5.63E+05 2.09E+03 2.73E+03 1.28E+06 2.49E+07 1.97E+03 9.56E+05 4.22E+04 3.67E+06 5.42E+06 4.67E+05 6.55E+03 8.12E+07 9.25E+03 1.20E+05 1.68E+07 5.98E+07 2.54E+07 8.16E+04 2.13E+03 5.14E+06 8.23E+02 8.23E+02 2.75E+02 9.40E+02 3.08E+03 3.72E+03 5.18E+03 1.34E+08 0.00E+00 0.00E+00 3.82E+06 6.06E+04 2.65E+02 1.56E+03 2.91E+03 6.03E+04 7.22E+06 6.79E+03 8.70E+05 5.96E+05 2.40E+03 4.15E+03 5.70E+02 1.43E+07 1.38E+07
ACCUMULATION STREAM Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
PT-Accumulation 7.35E+01 2.63E+04 9.47E-01 5.67E+00 1.23E+02 2.29E-01 5.35E+03 1.98E+00 3.69E+02 9.60E+01 1.48E+03 1.16E+01 3.30E+01 5.28E+02 1.25E+04 1.29E+00 1.63E+02 9.43E+01 4.58E-01 3.34E+02 3.69E+03 1.50E+00 3.09E+04 7.43E+01 1.02E+03 3.04E+03 4.02E+04 9.54E+03 5.87E+01 4.51E-02 2.41E+03 3.89E+00 5.06E+00 1.32E-02 2.52E+00 2.80E-01 1.52E+00 1.25E+00 7.27E+03 0.00E+00 0.00E+00 1.12E+03 7.48E+02 3.34E+00 1.56E-01 5.64E-01 2.03E+02 1.28E+01 2.32E+02 1.14E+02 6.53E+03 2.18E+01 6.20E-02 1.43E+00 1.94E+00 3.04E+03
TF-Accumulation 2.04E+02 4.64E+05 4.23E+00 2.53E+01 7.16E+02 3.32E-01 5.52E+04 1.98E+02 4.10E+02 5.98E+02 2.75E+04 9.09E-01 1.86E+02 6.24E+03 1.11E+05 1.73E+01 4.55E+02 2.49E+03 2.69E+00 1.66E+03 1.21E+04 3.51E+00 9.14E+04 4.50E+02 5.71E+03 6.42E+03 4.20E+04 6.24E+03 4.18E+02 7.34E+00 6.54E+04 2.06E+01 5.37E+01 3.50E+00 7.34E+00 5.08E+00 2.76E+00 2.71E+00 6.92E+04 0.00E+00 0.00E+00 2.67E+03 2.94E+03 6.06E+00 4.74E-01 3.00E+00 1.21E+03 1.15E+02 1.89E+02 7.69E+02 5.15E+04 1.77E+02 2.71E+00 1.08E+01 1.93E+01 1.82E+03
TRU-Accumulation 1.94E-02 2.91E+02 1.35E-02 2.92E-01 1.55E-01 6.08E-03 3.38E+02 9.73E-02 3.47E+00 1.25E+01 1.62E+01 1.47E-04 9.11E-01 1.57E+02 1.61E+02 2.34E-03 1.66E+00 1.96E-02 7.92E-115 2.52E+00 1.11E+00 3.96E-114 1.31E+03 7.92E-114 2.02E-01 3.37E+02 1.08E+03 1.08E-01 9.32E-01 0.00E+00 1.34E+03 0.00E+00 3.72E-02 0.00E+00 0.00E+00 1.13E-20 7.22E-01 8.75E-03 1.17E+02 0.00E+00 0.00E+00 7.15E+01 1.80E+00 0.00E+00 6.93E-04 0.00E+00 1.77E-08 1.73E-01 8.36E-113 5.54E+00 1.61E+01 2.50E-62 3.60E-299 6.08E-08 2.55E+00 1.21E+00
LAW Accumulation 3.24E-01 1.54E+03 2.65E-01 9.84E+02 2.29E-03 5.78E-02 7.90E+00 5.06E-01 1.60E+00 2.88E+01 8.72E+01 1.06E-05 4.61E-03 1.69E+02 1.25E+03 3.61E-01 2.41E+01 0.00E+00 1.17E-01 2.89E+02 0.00E+00 3.94E-01 8.59E+03 4.96E-01 3.82E-01 4.20E+02 1.82E+03 2.27E+03 5.65E+00 1.11E-02 3.78E+02 0.00E+00 4.78E-03 3.17E-03 0.00E+00 6.81E-02 4.16E-01 3.45E-01 6.65E+03 5.72E-03 8.26E+01 1.98E+02 1.12E-02 2.04E-05 4.37E-02 1.60E-01 0.00E+00 3.87E+02 0.00E+00 1.47E+01 9.71E-01 1.10E-04 1.54E-02 1.55E-02 7.66E+02 7.14E+02
HLW-Accumulation 8.86E-01 1.26E+03 5.62E-04 9.46E+02 7.92E+00 2.09E-04 3.29E+02 2.32E-03 1.84E+00 1.10E-02 3.25E+01 1.04E-01 2.16E+00 6.61E-02 7.61E+02 1.92E-03 5.88E-01 5.92E+00 3.44E+02 2.10E+01 2.41E+02 2.04E-03 6.20E+02 3.08E+00 4.98E+01 1.26E+00 4.67E+01 1.08E+01 3.96E-01 4.45E-05 1.36E-01 2.62E-01 3.09E-01 6.50E-06 1.67E-01 1.41E-04 4.39E-04 4.73E-04 2.47E+03 2.73E-05 7.36E-02 1.44E-01 2.90E+01 2.25E-01 1.57E-05 6.47E-04 1.14E+01 7.38E-01 1.11E+01 5.27E-02 3.52E+02 1.14E+00 6.12E-05 3.92E-02 2.85E-03 1.33E+02
SLAW-Accumulation 3.27E-01 1.33E+03 2.99E-01 8.85E+02 3.24E-03 6.39E-02 7.31E+00 4.61E-01 4.54E-01 3.48E+01 2.33E+01 1.28E-05 4.92E-03 2.20E+02 1.13E+03 4.27E-01 2.29E+01 0.00E+00 2.13E-01 2.60E+02 0.00E+00 4.79E-01 7.59E+03 4.44E-01 3.58E-01 4.26E+02 1.74E+03 1.84E+03 5.64E+00 1.16E-02 4.09E+02 0.00E+00 4.22E-03 3.18E-03 0.00E+00 6.99E-02 4.17E-01 3.95E-01 5.98E+03 1.29E-01 8.73E+01 3.45E+02 2.11E-02 1.99E-05 5.90E-02 1.92E-01 0.00E+00 3.48E+02 0.00E+00 1.52E+01 7.63E-01 1.04E-04 1.67E-02 1.38E-02 6.89E+02 6.43E+02
LAWPS-Accumulation 3.23E-04 1.84E+00 7.60E-03 1.49E-02 7.94E-07 3.53E-04 1.89E-02 4.57E-03 0.00E+00 1.04E+00 2.14E-01 2.37E-03 3.01E-04 1.19E-01 1.70E-02 5.11E-04 1.40E+00 0.00E+00 4.80E-03 0.00E+00 0.00E+00 8.01E-03 4.82E+01 1.92E-03 9.84E-04 1.59E+01 5.06E+01 1.05E+01 3.13E-02 1.82E-03 1.86E+00 0.00E+00 7.08E-05 1.14E-04 0.00E+00 2.23E-03 5.43E-03 6.92E-03 5.41E-02 0.00E+00 0.00E+00 1.24E+00 2.08E-05 3.70E-09 1.75E-03 3.72E-04 0.00E+00 0.00E+00 0.00E+00 5.97E-01 3.92E-03 3.75E-07 5.39E-03 5.87E-05 3.50E-03 0.00E+00
ETF-Accumulation 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00
LERF-Accumulation 2.49E-01 8.44E+01 3.42E+00 1.03E+00 1.91E-03 5.80E-02 1.01E+01 2.59E-01 2.16E+01 7.98E+02 2.38E+02 1.21E-04 3.65E-02 5.35E+03 2.88E+00 1.41E+01 7.46E+01 1.34E-21 1.51E-01 1.76E-22 1.54E-21 1.00E+00 1.01E+04 2.55E-01 1.78E-01 1.71E+00 5.43E+03 1.35E+03 4.96E+01 2.20E-02 5.96E+02 0.00E+00 1.86E-03 4.29E-03 0.00E+00 4.67E-02 2.99E+00 3.66E+00 1.42E+01 0.00E+00 0.00E+00 1.14E+04 1.37E-01 1.81E-05 8.56E-01 4.88E+00 1.67E-20 8.29E-23 1.35E-19 1.91E+01 3.69E-01 1.45E-04 2.09E-02 7.96E-03 4.05E-01 1.32E-22
Total Accumulation 2.79E+02 4.95E+05 9.18E+00 2.85E+03 8.47E+02 7.48E-01 6.12E+04 2.02E+02 8.08E+02 1.57E+03 2.94E+04 1.27E+01 2.22E+02 1.27E+04 1.27E+05 3.35E+01 7.44E+02 2.59E+03 3.47E+02 2.56E+03 1.60E+04 6.89E+00 1.51E+05 5.28E+02 6.78E+03 1.07E+04 9.23E+04 2.13E+04 5.39E+02 7.44E+00 7.06E+04 2.48E+01 5.92E+01 3.52E+00 1.00E+01 5.54E+00 8.82E+00 8.38E+00 9.17E+04 1.34E-01 1.70E+02 1.58E+04 3.72E+03 9.63E+00 1.59E+00 8.80E+00 1.43E+03 8.63E+02 4.32E+02 9.37E+02 5.84E+04 2.00E+02 2.83E+00 1.23E+01 1.48E+03 6.35E+03
Accumulation minus TF and TRU 7.52E+01 3.05E+04 4.94E+00 2.82E+03 1.31E+02 4.10E-01 5.70E+03 3.21E+00 3.94E+02 9.59E+02 1.86E+03 1.17E+01 3.52E+01 6.27E+03 1.57E+04 1.61E+01 2.87E+02 1.00E+02 3.45E+02 9.04E+02 3.93E+03 3.38E+00 5.79E+04 7.86E+01 1.07E+03 3.90E+03 4.93E+04 1.50E+04 1.20E+02 9.17E-02 3.80E+03 4.15E+00 5.38E+00 2.39E-02 2.69E+00 4.67E-01 5.34E+00 5.66E+00 2.24E+04 1.34E-01 1.70E+02 1.30E+04 7.77E+02 3.56E+00 1.12E+00 5.80E+00 2.15E+02 7.48E+02 2.43E+02 1.63E+02 6.88E+03 2.29E+01 1.20E-01 1.51E+00 1.46E+03 4.53E+03
ADJUSTED INVENTORY TO INCLUDE ACCUMULATION Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
LAW Glass Subtotal (IDF) 1.24E+03 1.95E+07 3.61E+03 1.83E+07 1.06E+01 4.93E+02 6.29E+04 6.99E+03 5.15E+04 4.09E+05 4.62E+05 4.59E-01 3.32E+02 5.84E+05 2.33E+07 0.00E+00 8.92E+05 3.73E-05 2.91E+06 5.39E+06 3.84E-05 6.39E+03 7.73E+07 3.29E+03 2.33E+03 0.00E+00 0.00E+00 0.00E+00 7.17E+04 2.11E+03 0.00E+00 0.00E+00 7.72E+01 2.69E+02 0.00E+00 3.05E+03 2.69E+03 3.88E+03 1.28E+08 #DIV/0! #DIV/0! 0.00E+00 8.83E+01 6.70E-02 1.06E+03 1.56E+03 4.67E-04 7.21E+06 1.10E-04 0.00E+00 7.97E+03 7.31E-01 4.11E+03 9.10E+01 1.43E+07 1.33E+07
LAW Spent Melter Subtotal (IDF) 1.71E+00 2.66E+04 4.27E+00 2.50E+04 1.97E-02 6.45E-01 8.78E+01 1.02E+01 7.65E+01 5.21E+02 6.41E+02 5.87E-04 3.69E-01 7.68E+02 3.18E+04 0.00E+00 1.06E+03 4.66E-08 4.14E+03 7.35E+03 4.79E-08 8.50E+00 1.05E+05 4.52E+00 3.06E+00 0.00E+00 0.00E+00 0.00E+00 9.57E+01 1.58E+00 0.00E+00 0.00E+00 1.05E-01 2.35E-01 0.00E+00 2.72E+00 3.34E+00 4.36E+00 1.75E+05 #DIV/0! #DIV/0! 0.00E+00 5.24E-02 1.16E-04 1.32E+00 2.14E+00 5.83E-07 9.84E+03 1.37E-07 2.44E-02 1.20E+01 1.07E-03 2.22E+00 1.25E-01 1.95E+04 1.82E+04
ETF Solid Waste Form to IDF 2.51E+01 1.14E+04 1.18E+03 1.62E+02 7.99E-01 5.65E+00 1.36E+03 6.33E+01 1.33E+03 3.69E+05 3.46E+04 8.95E-02 3.41E+01 6.09E+05 3.22E+02 1.65E+03 4.67E+04 2.74E-03 2.41E+01 1.14E+00 3.41E+01 1.38E+02 1.76E+06 3.45E+01 2.38E+01 2.17E+04 2.23E+06 8.73E+04 7.18E+03 2.18E+01 5.50E+04 0.00E+00 7.01E-01 5.58E+00 0.00E+00 3.09E+01 8.77E+02 1.26E+03 1.41E+03 #DIV/0! #DIV/0! 9.29E+05 1.15E+01 1.04E-03 4.99E+02 5.16E+02 4.24E-06 1.08E-05 5.04E-05 5.16E+03 8.07E+01 1.46E-04 2.09E-02 7.98E-03 3.17E+01 1.42E-05
Solid Waste Forms from Treatment Processes (IDF) 9.67E-02 2.28E+01 2.51E-01 2.97E+01 3.55E-02 5.27E-05 2.45E-02 4.63E-01 7.56E-04 4.45E+04 6.94E+02 1.95E-01 3.23E-03 5.50E+04 1.48E-01 3.24E+02 2.96E+02 8.76E-07 1.19E-01 8.84E-03 8.53E-02 1.42E-02 4.55E+03 3.02E-05 5.54E-01 0.00E+00 0.00E+00 0.00E+00 1.25E+01 2.25E-04 3.99E+03 6.89E-07 3.60E-04 1.06E-03 7.88E-07 7.70E-03 8.69E-03 4.15E-01 1.68E-01 #DIV/0! #DIV/0! 0.00E+00 3.54E-02 2.30E-07 6.60E-01 2.56E-02 5.06E-05 2.85E-04 1.48E-04 0.00E+00 1.34E-03 2.87E-05 4.39E-04 2.64E-06 1.63E-01 3.21E-02
Non-IDF Stream 2.55E+03 2.48E+06 8.53E+01 1.50E+06 8.69E+03 2.71E+00 4.82E+05 1.61E+03 6.65E+03 4.51E+03 6.58E+04 2.09E+03 2.36E+03 3.03E+04 1.54E+06 -2.72E+00 1.64E+04 4.22E+04 7.51E+05 2.28E+04 4.67E+05 2.25E+01 2.04E+06 5.92E+03 1.17E+05 1.68E+07 5.76E+07 2.53E+07 2.65E+03 5.16E-01 5.08E+06 8.23E+02 7.45E+02 8.53E-02 9.40E+02 5.12E-01 1.56E+02 3.09E+01 5.57E+06 #DIV/0! #DIV/0! 2.89E+06 6.05E+04 2.65E+02 3.72E-01 8.36E+02 6.03E+04 1.38E+03 6.78E+03 8.65E+05 5.88E+05 2.40E+03 4.40E+01 4.79E+02 4.31E+02 4.04E+05
3.82E+03 2.20E+07 4.87E+03 1.99E+07 8.70E+03 5.02E+02 5.46E+05 8.67E+03 5.96E+04 8.28E+05 5.63E+05 2.09E+03 2.72E+03 1.28E+06 2.49E+07 1.97E+03 9.56E+05 4.22E+04 3.67E+06 5.42E+06 4.67E+05 6.55E+03 8.12E+07 9.25E+03 1.20E+05 1.68E+07 5.98E+07 2.54E+07 8.16E+04 2.13E+03 5.14E+06 8.23E+02 8.23E+02 2.75E+02 9.40E+02 3.08E+03 3.72E+03 5.18E+03 1.34E+08 #DIV/0! #DIV/0! 3.82E+06 6.06E+04 2.65E+02 1.56E+03 2.91E+03 6.03E+04 7.22E+06 6.78E+03 8.70E+05 5.96E+05 2.40E+03 4.15E+03 5.70E+02 1.43E+07 1.38E+07
100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% #DIV/0! #DIV/0! 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100%
SSW FRACTIONS BASED ON 10-010 and 10-009 Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
HEPA fraction 4.53% 17.39% 17.89% 62.10% 6.43% 0.15% 5.17% 50.79% 0.21% 0.00% 94.18% NR 0.00% 0.00% 44.22% 0.00% 56.46% 7.86% 91.84% 69.10% 12.79% NR 40.68% 4.20% 13.13% NR NR NR 61.05% 1.03% NR #DIV/0! 8.09% 5.61% 5.04% 78.35% 5.42% 31.35% 41.49% NR NR NR 15.98% 0.00% 63.36% 20.43% 7.69% 71.77% 23.04% NR 8.06% 41.24% 0.23% NR 87.47% 60.66%
IX Resin fraction 43.06% 62.12% 53.58% 0.54% 22.10% 93.91% 29.47% 23.43% 90.28% 95.63% 5.35% NR 0.00% 0.08% 0.00% 0.00% 42.37% 5.18% 0.04% 0.12% 0.00% NR 55.24% 45.56% 38.04% NR NR NR 19.53% 83.67% NR #DIV/0! 0.00% 61.81% 76.38% 0.00% 72.52% 63.57% 0.12% NR NR NR 0.23% 0.00% 34.99% 4.19% 25.51% 0.00% 38.40% NR 0.00% 16.62% 93.95% NR 0.01% 0.38%
LAW and HLW Carbon Bed fraction 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 98.32% 0.00% 100.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% NR #DIV/0! 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0.00% 0.00% NR 0.00% 0.00%
Other Debris fraction 52.41% 20.48% 28.53% 37.37% 71.47% 5.95% 65.36% 25.78% 9.52% 4.37% 0.47% NR 100.00% 0.01% 55.78% 0.00% 1.17% 86.96% 8.12% 30.78% 87.21% NR 4.08% 50.24% 48.83% NR NR NR 19.42% 15.31% NR #DIV/0! 91.91% 32.59% 18.58% 21.65% 22.06% 5.08% 58.40% NR NR NR 83.79% 100.00% 1.65% 75.39% 66.80% 28.23% 38.56% NR 91.94% 42.15% 5.83% NR 12.52% 38.96%
HLW Silver Mordenite Absorbent fraction 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 1.59% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% NR #DIV/0! 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR NR NR 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% NR 0.00% 0.00% 0.00% NR 0.00% 0.00%
WTP SSW INVENTORY Ag Al As B Ba Be Bi Cd Ce Cl Cr Cs Cu F Fe Hg K La Li Mg Mn Mo Na Nd Ni NO2- NO3- OH- Pb Pd PO4-3 Pr Pu Rb Rh Ru Sb Se Si SO2 SO3 SO4-2 Sr Ta Tc Te Th Ti Tl TOC U V W Y Zn Zr
HEPA Filters Debris 4.38E-03 3.96E+00 4.50E-02 1.84E+01 2.28E-03 7.70E-08 1.26E-03 2.35E-01 1.57E-06 0.00E+00 6.54E+02 NR 0.00E+00 8.71E-02 6.53E-02 0.00E+00 1.67E+02 6.89E-08 1.09E-01 6.11E-03 1.09E-02 NR 1.85E+03 1.27E-06 7.28E-02 NR NR NR 7.61E+00 2.32E-06 NR #DIV/0! 2.91E-05 5.97E-05 3.97E-08 6.04E-03 4.71E-04 1.30E-01 6.99E-02 NR NR NR 5.65E-03 0.00E+00 4.18E-01 5.23E-03 3.89E-06 2.05E-04 3.42E-05 NR 1.08E-04 1.18E-05 9.97E-07 NR 1.42E-01 1.95E-02
IX Resin Non-Debris 4.16E-02 1.42E+01 1.35E-01 1.59E-01 7.85E-03 4.95E-05 7.21E-03 1.09E-01 6.83E-04 4.26E+04 3.72E+01 NR 0.00E+00 4.64E+01 5.88E-07 7.25E-03 1.25E+02 4.54E-08 4.33E-05 1.02E-05 1.88E-08 NR 2.52E+03 1.38E-05 2.11E-01 NR NR NR 2.43E+00 1.89E-04 NR #DIV/0! 7.51E-09 6.58E-04 6.02E-07 1.14E-08 6.30E-03 2.64E-01 2.00E-04 NR NR NR 8.12E-05 0.00E+00 2.31E-01 1.07E-03 1.29E-05 4.96E-12 5.69E-05 NR 1.33E-09 4.77E-06 4.12E-04 NR 1.27E-05 1.22E-04
LAW and HLW Carbon Beds Non-Debris 1.11E-12 2.66E-09 6.34E-11 1.37E-08 3.08E-13 1.17E-15 1.99E-13 3.52E-10 1.57E-14 2.34E-02 6.78E-10 NR 0.00E+00 5.40E+04 3.88E-11 3.24E+02 1.02E-07 1.52E-18 6.57E-11 3.67E-12 1.09E-11 NR 1.17E-06 3.26E-16 6.52E-11 NR NR NR 5.65E-09 4.51E-15 NR #DIV/0! 4.03E-16 3.39E-14 3.16E-17 1.72E-11 5.68E-13 1.37E-10 4.19E-11 NR NR NR 1.00E-11 0.00E+00 2.58E-10 8.57E-12 1.06E-15 1.23E-13 1.59E-14 NR 1.51E-15 7.04E-15 9.77E-15 NR 8.49E-11 1.17E-11
Other Debris Debris 5.07E-02 4.67E+00 7.18E-02 1.11E+01 2.54E-02 3.13E-06 1.60E-02 1.20E-01 7.20E-05 1.94E+03 3.24E+00 NR 3.23E-03 2.88E+00 8.23E-02 6.50E-04 3.47E+00 7.62E-07 9.68E-03 2.72E-03 7.43E-02 NR 1.86E+02 1.52E-05 2.71E-01 NR NR NR 2.42E+00 3.45E-05 NR #DIV/0! 3.31E-04 3.47E-04 1.46E-07 1.67E-03 1.92E-03 2.11E-02 9.84E-02 NR NR NR 2.96E-02 2.30E-07 1.09E-02 1.93E-02 3.38E-05 8.05E-05 5.72E-05 NR 1.23E-03 1.21E-05 2.56E-05 NR 2.04E-02 1.25E-02
HLW Silver Mordenite Absorbent Non-Debris 8.95E-14 8.77E-11 9.30E-11 1.57E-10 1.24E-13 1.57E-19 2.82E-14 5.38E-10 5.11E-17 1.21E-07 5.71E-10 NR 0.00E+00 8.74E+02 2.88E-13 2.56E-03 1.48E-09 9.51E-19 1.36E-13 2.38E-14 1.88E-11 NR 2.01E-09 1.81E-17 7.07E-11 NR NR NR 2.89E-09 5.94E-17 NR #DIV/0! 8.06E-16 1.43E-15 3.64E-19 3.44E-11 5.62E-13 1.36E-10 1.73E-13 NR NR NR 2.01E-11 0.00E+00 2.17E-13 1.69E-11 7.50E-17 8.73E-16 1.85E-15 NR 3.03E-15 5.29E-17 2.95E-19 NR 1.51E-15 4.26E-14
SSW Total 9.67E-02 2.28E+01 2.51E-01 2.97E+01 3.55E-02 5.27E-05 2.45E-02 4.63E-01 7.56E-04 4.45E+04 6.94E+02 NR 3.23E-03 5.50E+04 1.48E-01 3.24E+02 2.96E+02 8.76E-07 1.19E-01 8.84E-03 8.53E-02 NR 4.55E+03 3.02E-05 5.54E-01 NR NR NR 1.25E+01 2.25E-04 NR #DIV/0! 3.60E-04 1.06E-03 7.88E-07 7.70E-03 8.69E-03 4.15E-01 1.68E-01 NR NR NR 3.54E-02 2.30E-07 6.60E-01 2.56E-02 5.06E-05 2.85E-04 1.48E-04 NR 1.34E-03 2.87E-05 4.39E-04 NR 1.63E-01 3.21E-02
BBI 5.91E+05 1.99E+03 8.20E+04
Check 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% 100% N/A 100% 100% 100% 100% 100% 100% 100% 100% 100% N/A 100% 100% 100% N/A N/A N/A 100% 100% N/A #DIV/0! 100% 100% 100% 100% 100% 100% 100% N/A N/A N/A 100% 100% 100% 100% 100% 100% 100% N/A 100% 100% 100% N/A 100% 100%
SE
CT
ION
1S
EC
TIO
N 2
SE
CT
ION
3A
SE
CT
ION
4S
EC
TIO
N 5
A
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ENGINEERING CALCULATION DOCUMENTATION
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APPENDIX B
ENGINEERING CALCULATION DOCUMENTATION
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Page 1 of 3 A-6003-508 (REV 4)
INFORMATION CLEARANCE REVIEW AND RELEASE APPROVAL
Part I: Background Information
Title: Information Category:
Abstract Journal Article Summary
Internet Visual Aid Software
Publish to OSTI? Yes No Full Paper Report Other
Trademark/Copyright “Right to Use” Information or Permission Documentation
Yes NA
Document Number: Date:
Author:
Part II: External/Public Presentation Information Conference Name:
Sponsoring Organization(s):
Date of Conference: Conference Location:
Will Material be Handed Out? Yes No Will Information be Published? Yes No (If Yes, attach copy of Conference format instructions/guidance.)
Part III: WRPS Document Originator Checklist
Description Yes N/A Print/Sign/Date
Information Product meets requirements in TFC-BSM-AD-C-01?
Document Release Criteria in TFC-ENG-DESIGN-C-25 completed? (Attach checklist)
If product contains pictures, safety review completed?
Part IV: WRPS Internal Review
Function Organization Date Print Name/Signature/Date
Subject Matter Expert
Responsible Manager
Other:
Part V: IRM Clearance Services Review
Description Yes No Print Name/Signature
Document Contains Classified Information? If Answer is “Yes,” ADC Approval Required
Print Name/Signature/Date
Document Contains Information Restricted by DOE Operational Security Guidelines?
Reviewer Signature:
Print Name/Signature/Date
Document is Subject to Release Restrictions? Document contains:
If the answer is “Yes,” please mark category at right and describe limitation or responsible organization below:
Applied Technology Protected CRADA
Personal/Private Export Controlled
Proprietary Procurement – Sensitive
Patentable Info. OUO
Predecisional Info. UCNI
Restricted by Operational Security Guidelines
Other (Specify)
Additional Comments from Information Clearance Specialist Review?
Information Clearance Specialist Approval
Print Name/Signature/Date When IRM Clearance Review is Complete – Return to WRPS Originator for Final Signature Routing (Part VI)
Inventory Data Summary for the Integrated Disposal Facility Performance Assessment
RPP-ENV-58562 Revision 3 May 2016
Lee, Kearn (Pat)
Not Applicable
Not Applicable
Not Applicable Not Applicable
✔
Lee, Kearn (Pat)
WRPS
WRPS
Lee, Kearn (Pat)
Rutland, Paul L
✔ ✔
✔
✔
✔
✔
✔
Lee, Kearn (Pat)
IDMS Data File att.IDMS Data File att.
09/23/201608/31/2016
x
x
x
x
IDMS Data File att.IDMS Data File att.
By Lana Perry at 7:40 am, Sep 26, 2016
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Page 2 of 3 A-6003-508 (REV 4)
INFORMATION CLEARANCE REVIEW AND RELEASE APPROVAL
Part VI: Final Review and Approvals
Description Approved for Release
Print Name/Signature Yes N/A
WRPS External Affairs
WRPS Office of Chief Counsel
DOE – ORP Public Affairs/Communications
Other:
Other:
Comments Required for WRPS-Indicate Purpose of Document:
Information Release Station
Was/Is Information Product Approved for Release? Yes No
If Yes, what is the Level of Releaser? Public/Unrestricted Other (Specify)
Date Information Product Stamped/Marked for Release:
Was/Is Information Product Transferred to OSTI? Yes No
Forward Copies of Completed Form to WRPS Originator
Holloway, Jerry NRoden, Mari L
Marshall, Richard
Pyles, Gary L
✔
The report is a data package that supplies input values to be used in the 2017 Integrated Disposal Facility Performance Assessment. The Washington Department of Ecology is a stakeholder in the development of the work product and ORP has requested that the data packages be shared with Ecology.
x
xxxORP
IDMS Data File att.IDMS Data File att.IDMS Data File att.IDMS Data File att.
By Lana Perry at 7:44 am, Sep 26, 2016
Approved for Public Release; Further Dissemination Unlimited
X
X
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- <workflow name="(LRP)Normal - RPP-ENV-58562 R3_Inv Data Sum IDF PA"id="210153479">
- <task name="Clearance Process" id="0" date-initiated="20160831T0945"performer="Lana R Perry" performer-id="86772" username="h0028549"><comments>Due Wednesday 09-07-2016 COB Please approve Inventory
Data Summary for the Integrated Disposal Facility Performance Assessment, submitted by Kearn (Pat) Lee for public release. Thank you, Lana Perry Information Clearance</comments>
</task><task name="Add XML" id="1" date-done="20160831T0945" /><task name="Manager Approval" id="41" date-due="20160905T0945" date-
done="20160831T1012" performer="Paul L Rutland" performer-id="140633218"username="h4494439" disposition="Approve" authentication="true" />
<task name="Document Reviewer3" id="52" date-due="20160905T1012" date-done="20160901T1107" performer="Gary L Pyles" performer-id="147601648"username="h6400308" disposition="Public Release" authentication="true" />
<task name="Document Reviewer2" id="53" date-due="20160905T1012" date-done="20160907T1655" performer="Mari L Roden" performer-id="179713158"username="h0048955" disposition="Public Release" authentication="true" />
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<task name="Doc Owner Clearance Review" id="13" date-due="20160913T1321"date-done="20160921T0616" performer="Kearn P Lee" performer-id="148796764" username="h8500694" disposition="Send On"authentication="true" />
<task name="Milestone 1" id="24" date-done="20160921T0616" />- <task name="ORP Document Reviewer1" id="57" date-due="20160923T0616"
date-done="20160922T1528" performer="Richard A Marshall" performer-id="203862915" username="h4535783" disposition="Public Release"authentication="true"><reviewer performer="Gary L Pyles" performer-id="147601648"
username="h6400308" /></task>
- <task name="Doc Owner Reviews ORP Comments" id="61" date-due="20160923T1528" date-done="20160922T1533" performer="Kearn P Lee"performer-id="148796764" username="h8500694" disposition="Send On"authentication="true"><comments>There were no comments provided and no additional red-line
strike out files in the attachments.</comments></task><task name="Milestone 2" id="62" date-done="20160922T1534" /><task name="Verify Doc Consistency" id="4" date-due="20160923T1533" date-
done="20160926T0731" performer="Lana R Perry" performer-id="86772"username="h0028549" disposition="Cleared" authentication="true" />
</workflow>
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RPP-ENV-58562Revision 3
Copy No.
Inventory Data Summary for the Integrated Disposal Facility Performance Assessment
Prepared for the U.S. Department of EnergyAssistant Secretary for Environmental Management
Contractor for the U.S. Department of EnergyOffice of River Protection under Contract DE-AC27-08RV14800
P.O. Box 850 Richland, Washington 99352
Approved for Public Release; Further Dissemination Unlimited
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Copy No.
Inventory Data Summary for the Integrated DisposalFacility Performance Assessment
K. A. PrindivilleWashington River Protection Solutions
Date PublishedMay 2016
To be Presented atNot Applicable
Not ApplicableNot Applicable
Not Applicable
Published inNot Applicable
Prepared for the U.S. Department of EnergyAssistant Secretary for Environmental Management
Contractor for the U.S. Department of EnergyOffice of River Protection under Contract DE-AC27-08RV14800
P.O. Box 850 Richland, Washington 99352
Copyright License By acceptance of this article, the publisher and/or recipient acknowledges the U.S. Government's right to retain a non exclusive, royalty-free licensein an to any copyright covering this paper.
Release Approval Date
Approved for Public Release; Further Dissemination Unlimited
By Lana Perry at 7:48 am, Sep 26, 2016
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LEGAL DISCLAIMERThis report was prepared as an account of work sponsored by an agency ofthe United States Government. Neither the United States Government norany agency thereof, nor any of their employees, makes any warranty,express or implied, or assumes any legal liability or responsibility for theaccuracy, completeness, or any third party's use or the results of such useof any information, apparatus, product, or process disclosed, or representsthat its use would not infringe privately owned rights. Reference herein toany specific commercial product, process, or service by trade name,trademark, manufacturer, or otherwise, does not necessarily constitute orimply its endorsement, recommendation, or favoring by the United StatesGovernment or any agency thereof or its contractors or subcontractors. Theviews and opinions of authors expressed herein do not necessarily state orreflect those of the United States Government or any agency thereof.
This report has been reproduced from the best available copy.
Printed in the United States of America
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