ML23304A361

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LLC Revision 1 to Standard Design Approval Application, Part 2, Chapter 12, Radiation Protection
ML23304A361
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Site: 05200050
Issue date: 10/31/2023
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NuScale
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Office of Nuclear Reactor Regulation
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LO-151262
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NuScale US460 Plant Standard Design Approval Application Chapter Twelve Radiation Protection Final Safety Analysis Report Revision 1

©2023, NuScale Power LLC. All Rights Reserved

document bears a NuScale Power, LLC, copyright notice. No right to disclose, use, or copy of the information in this document, other than by the U.S. Nuclear Regulatory Commission C), is authorized without the express, written permission of NuScale Power, LLC.

NRC is permitted to make the number of copies of the information contained in these reports ded for its internal use in connection with generic and plant-specific reviews and approvals, well as the issuance, denial, amendment, transfer, renewal, modification, suspension, ocation, or violation of a license, permit, order, or regulation subject to the requirements of 10 R 2.390 regarding restrictions on public disclosure to the extent such information has been tified as proprietary by NuScale Power, LLC, copyright protection notwithstanding.

arding nonproprietary versions of these reports, the NRC is permitted to make the number of itional copies necessary to provide copies for public viewing in appropriate docket files in lic document rooms in Washington, DC, and elsewhere as may be required by NRC ulations. Copies made by the NRC must include this copyright notice in all instances and the prietary notice if the original was identified as proprietary.

APTER 12 RADIATION PROTECTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.1-1 12.1 Ensuring that Occupational Radiation Exposures Are as Low as Reasonably Achievable . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.1-1 12.1.1 Policy Considerations . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.1-1 12.1.2 Design Considerations . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.1-1 12.1.3 Operational Considerations . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.1-5 12.2 Radiation Sources . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-1 12.2.1 Contained Sources . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-1 12.2.2 Airborne Radioactive Material Sources . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-7 12.2.3 References . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-9 12.3 Radiation Protection Design Features . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-1 12.3.1 Facility Design Features . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-1 12.3.2 Shielding. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-8 12.3.3 Ventilation. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-14 12.3.4 Area Radiation and Airborne Radioactivity Monitoring Instrumentation. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-17 12.3.5 Dose Assessment . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-23 12.3.6 Minimization of Contamination and Radioactive Waste Generation. . . 12.3-23 12.3.7 References . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-26 12.4 Dose Assessment . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.4-1 12.4.1 Occupational Radiation Exposure . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.4-1 12.4.2 Radiation Exposure at the Restricted Area Boundary . . . . . . . . . . . . . . 12.4-4 12.5 Operational Radiation Protection Program . . . . . . . . . . . . . . . . . . . . . . . . . . 12.5-1 cale US460 SDAA i Revision 1

le 12.2-1: Core and Coolant Source Information . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-10 le 12.2-2: Primary Coolant at the Steam Generator Entrance Gamma Source Term . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-11 le 12.2-3: Primary Coolant at the Core Exit Gamma Source Term . . . . . . . . . . . . . 12.2-13 le 12.2-4: Nitrogen-16 Primary Coolant Concentrations at Full Power . . . . . . . . . . 12.2-15 le 12.2-5: Chemical and Volume Control System Component Source Term Inputs and Assumptions. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-16 le 12.2-6: Chemical and Volume Control System Component Source Terms

-Radionuclide Content . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-17 le 12.2-7: Chemical and Volume Control System Component Source Terms - Source Strengths . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-20 le 12.2-8: Pool Cooling and Cleanup System Component Source Term Inputs and Assumptions. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-22 le 12.2-9: Pool Cooling and Cleanup System Component Source Terms - Radionuclide Content . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-23 le 12.2-10: Pool Cooling and Cleanup System Component Source Terms - Source Strengths . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-26 le 12.2-11: Liquid Radioactive Waste System Component Source Term Inputs and Assumptions . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-28 le 12.2-12a: Liquid Radioactive Waste System Component Source Terms - Radionuclide Content . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-30 le 12.2-12b: Liquid Radioactive Waste System Component Source Terms - Radionuclide Content . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-33 le 12.2-12c: Liquid Radioactive Waste System Component Source Terms - Radionuclide Content . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-36 le 12.2-13a: Liquid Radioactive Waste System Component Source Terms - Source Strengths . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-39 le 12.2-13b: Liquid Radioactive Waste System Component Source Terms - Source Strengths . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-41 le 12.2-13c: Liquid Radioactive Waste System Component Source Terms - Source Strengths . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-43 le 12.2-14: Gaseous Radioactive Waste System Component Source Term Inputs . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-45 le 12.2-15: Gaseous Radioactive Waste System Component Source Term Radionuclide Content. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-46 le 12.2-15a: Degasifier Radiological Content . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-49 le 12.2-16: Gaseous Radioactive Waste System Component Source Terms - Source Strengths . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-52 cale US460 SDAA ii Revision 1

le 12.2-17: Solid Radioactive Waste System Source Term Inputs . . . . . . . . . . . . . . 12.2-54 le 12.2-18: Solid Radioactive Waste System Component Source Terms - Radionuclide Content . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-55 le 12.2-19: Solid Radioactive Waste System Component Source Terms - Source Strengths . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-58 le 12.2-20: Spent Fuel Gamma Source Strength. . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-60 le 12.2-21: Spent Fuel Neutron Energy Spectrum . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-62 le 12.2-22: In-Core Instrument Source Term Input Assumptions. . . . . . . . . . . . . . . . 12.2-63 le 12.2-23: In-Core Instrumentation Gamma Spectra . . . . . . . . . . . . . . . . . . . . . . . . 12.2-64 le 12.2-24: Control Rod Assembly Tip Source Term Input Assumptions. . . . . . . . . . 12.2-65 le 12.2-25: Control Rod Assembly Tip Gamma Spectra (End of Cycle 1) . . . . . . . . . 12.2-66 le 12.2-26: Secondary Neutron Source Gamma Spectra (End of Cycle 1) . . . . . . . . 12.2-67 le 12.2-27: Post-Accident Equipment Qualification Source Term Input Assumptions . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-68 le 12.2-28: Post-Accident Integrated Energy Deposition and Integrated Dose . . . . . 12.2-69 le 12.2-29: Input Parameters for Determining Facility Airborne Concentrations . . . . 12.2-70 le 12.2-30: Reactor Building Airborne Concentrations. . . . . . . . . . . . . . . . . . . . . . . . 12.2-71 le 12.2-31: Maximum Post-Accident Radionuclide Concentrations . . . . . . . . . . . . . . 12.2-74 le 12.3-1: Normal Operation Radiation Zone Designations . . . . . . . . . . . . . . . . . . . 12.3-28 le 12.3-2: Airborne Radiation Zone Designations . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-29 le 12.3-3: Typical Cobalt Content of Materials . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-30 le 12.3-4a: Reactor Building Areas of Potential Airborne Radioactive Material . . . . . 12.3-31 le 12.3-4b: Radioactive Waste Building Areas of Potential Airborne Radioactive Material . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-32 le 12.3-5: Reactor Building Shield Wall Geometry. . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-33 le 12.3-6: Radioactive Waste Building Shield Wall Geometry . . . . . . . . . . . . . . . . . 12.3-37 le 12.3-7: Radioactive Waste Building Radiation Shield Doors . . . . . . . . . . . . . . . . 12.3-39 le 12.3-8: Fixed Area and Airborne Radiation Monitors Post-Accident Monitoring Variables . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-40 le 12.3-9: Fixed Airborne Radiation Monitors. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-41 le 12.3-10: Fixed Area Radiation Monitors. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-42 le 12.3-11: NuScale Power Plant Systems with Nuclear Regulatory Commission Regulatory Guide 4.21 Evaluation . . . . . . . . . . . . . . . . . . . 12.3-44 cale US460 SDAA iii Revision 1

le 12.3-12: Regulatory Guide 4.21 Design Features for Auxiliary Boiler System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-45 le 12.3-13: Regulatory Guide 4.21 Design Features for Air Cooled Condenser System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-46 le 12.3-14: Regulatory Guide 4.21 Design Features for Balance-of-Plant Drain System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-47 le 12.3-15: Regulatory Guide 4.21 Design Features for Containment Evacuation System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-48 le 12.3-16: Regulatory Guide 4.21 Design Features for Containment Flooding and Drain System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-49 le 12.3-17: Regulatory Guide 4.21 Design Features for Chilled Water System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-50 le 12.3-18: Regulatory Guide 4.21 Design Features for Condensate Polisher Resin Regeneration System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-51 le 12.3-19: Regulatory Guide 4.21 Design Features for Normal Control Room Ventilation System. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-52 le 12.3-20: Regulatory Guide 4.21 Design Features for Chemical and Volume Control System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-53 le 12.3-21: Regulatory Guide 4.21 Design Features for Decay Heat Removal System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-54 le 12.3-22: Regulatory Guide 4.21 Design Features for Demineralized Water System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-55 le 12.3-23: Regulatory Guide 4.21 Design Features for Condensate and Feedwater System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-56 le 12.3-24: Regulatory Guide 4.21 Design Features for Gaseous Radioactive Waste System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-57 le 12.3-25: Regulatory Guide 4.21 Design Features for Liquid Radioactive Waste System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-58 le 12.3-26: Regulatory Guide 4.21 Design Features for Main Steam System . . . . . . 12.3-60 le 12.3-27: Regulatory Guide 4.21 Design Features for Pool Cooling and Cleanup System. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-61 le 12.3-28: Regulatory Guide 4.21 Design Features for Pool Leakage Detection System. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-63 le 12.3-29: Regulatory Guide 4.21 Design Features for Process Sampling System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-64 le 12.3-30: Regulatory Guide 4.21 Design Features for Reactor Building Heating, Ventilation, and Air Conditioning System . . . . . . . . . . . . . . . . . 12.3-66 cale US460 SDAA iv Revision 1

le 12.3-31: Regulatory Guide 4.21 Design Features for Reactor Component Cooling Water System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-67 le 12.3-32: Regulatory Guide 4.21 Design Features for Reactor Coolant System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-68 le 12.3-33: Regulatory Guide 4.21 Design Features for Radioactive Waste Building Heating, Ventilation, and Air Conditioning System. . . . . . . . . . . 12.3-69 le 12.3-34: Regulatory Guide 4.21 Design Features for Radioactive Waste Building . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-70 le 12.3-35: Regulatory Guide 4.21 Design Features for Radioactive Waste Drain System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-71 le 12.3-36: Regulatory Guide 4.21 Design Features for Reactor Building . . . . . . . . . 12.3-73 le 12.3-37: Regulatory Guide 4.21 Design Features for Site Cooling Water System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-74 le 12.3-38: Regulatory Guide 4.21 Design Features for Solid Radioactive Waste System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-75 le 12.3-39: Regulatory Guide 4.21 Design Features for Ultimate Heat Sink . . . . . . . 12.3-77 le 12.3-40: Regulatory Guide 4.21 Design Features for Utility Water System . . . . . . 12.3-78 le 12.4-1: Estimated Total Annual Occupational Radiation Exposures . . . . . . . . . . . 12.4-5 le 12.4-2: Occupational Dose Estimates from Reactor Operations and Surveillance . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.4-6 le 12.4-3: Occupational Dose Estimates from Routine Inspection and Maintenance . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.4-7 le 12.4-4: Occupational Dose Estimates from Inservice Inspection. . . . . . . . . . . . . . 12.4-8 le 12.4-5: Occupational Dose Estimates from Special Maintenance . . . . . . . . . . . . . 12.4-9 le 12.4-6: Occupational Dose Estimates from Waste Processing . . . . . . . . . . . . . . 12.4-10 le 12.4-7: Occupational Dose Estimates from Refueling Activities . . . . . . . . . . . . . 12.4-11 cale US460 SDAA v Revision 1

ure 12.3-1a: Reactor Building Radiation Zone Map - 25' Elevation . . . . . . . . . . . . . . . 12.3-79 ure 12.3-1b: Reactor Building Radiation Zone Map - 40 Elevation . . . . . . . . . . . . . . . 12.3-80 ure 12.3-1c: Reactor Building Radiation Zone Map - 55' Elevation . . . . . . . . . . . . . . . 12.3-81 ure 12.3-1d: Reactor Building Radiation Zone Map - 70' Elevation . . . . . . . . . . . . . . . 12.3-82 ure 12.3-1e: Reactor Building Radiation Zone Map - 85' Elevation . . . . . . . . . . . . . . . 12.3-83 ure 12.3-1f: Reactor Building Radiation Zone Map - 100' Elevation . . . . . . . . . . . . . . 12.3-84 ure 12.3-1g: Reactor Building Radiation Zone Map - 126' Elevation . . . . . . . . . . . . . . 12.3-85 ure 12.3-1h: Reactor Building Radiation Zone Map - 145' 6" Elevation . . . . . . . . . . . . 12.3-86 ure 12.3-2a: Radioactive Waste Building Radiation Zone Map - 70' Elevation . . . . . . 12.3-87 ure 12.3-2b: Radioactive Waste Building Radiation Zone Map - 82' Elevation . . . . . . 12.3-88 ure 12.3-2c: Radioactive Waste Building Radiation Zone Map - 100' Elevation . . . . . 12.3-89 cale US460 SDAA vi Revision 1

1 Ensuring that Occupational Radiation Exposures Are as Low as Reasonably Achievable Plant design features, administrative programs, and procedures assist in maintaining occupational radiation exposure as low as reasonably achievable (ALARA) in accordance with 10 CFR 20.1101. The purpose of this chapter is to describe the policies, programs, and features for radiation protection.

1.1 Policy Considerations 1.1.1 Design and Construction Policies The design incorporates ALARA principles and policies. Design reviews integrate facility layout, radiation shielding, building ventilation, material selection, and instrumentation design with layout requirements, flow of personnel, plant security, access control, and health physics considerations.

1.1.2 Operational Policies Section 12.1.3 addresses implementation of the operational ALARA policy.

1.1.3 Compliance with 10 CFR 20 and Regulatory Guides 8.8, 8.10, and 1.8 The design complies with 10 CFR 20, and Regulatory Guides (RG) 8.8, Revision 3 and 8.10, Revision 1-R. Section 12.1.3 and Section 12.5 discuss plant operation policy considerations described in RG 8.8, RG 8.10, and RG 1.8, Revision 3 and demonstrated by an application that references the NuScale Power Plant US460 standard design. The design meets the guidance of RG 8.8, Sections C.2 and C.4 that address facility, equipment, and instrumentation design features. Section 12.3 addresses plant features that are examples of compliance with RG 8.8.

1.2 Design Considerations This section describes the methods and features that allow the policy considerations of Section 12.1.1 to be implemented. Section 12.3 presents design features and attributes for maintaining ALARA personnel exposures.

1.2.1 General Design Considerations for Maintaining Exposures as Low as Reasonably Achievable Experienced engineers use an inter-disciplinary ALARA design review process to ensure the design conforms to 10 CFR 20.1101(b) and RG 8.8. The design engineers receive training in radiation science and in ALARA design concepts that are incorporated into the facility design. During the design work, calculations are developed for the radiation source terms, radiation shielding, radiation zone cale US460 SDAA 12.1-1 Revision 1

engineers during multi-discipline design phase reviews, which are used to develop additional ALARA features, as necessary.

The ALARA philosophy guiding the design ensures exposures are minimized by designing structures, systems, and components to achieve the following objectives:

  • attain optimal reliability and maintainability, thereby reducing maintenance requirements for radioactive components.
  • reduce radiation fields, thereby allowing operations, maintenance, and inspection activities to be performed in reduced radiation fields.
  • reduce access, repair, and equipment removal times, thereby reducing the time spent in radiation fields.
  • accommodate remote and semi-remote operation, maintenance, and inspection, thereby reducing the time spent in radiation fields.

To minimize production, distribution, and retention of activated corrosion products, the design considerations include appropriate material selection and proper water chemistry. Section 12.1.2.2 describes the design considerations in more detail.

Section 12.3 describes design considerations and features addressing 10 CFR 20.1406 to minimize contamination of the facility, environment, waste generation, and decommissioning.

1.2.2 Equipment Design Considerations for Maintaining Exposures as Low as Reasonably Achievable 1.2.2.1 General Design Criteria The engineering design process requires consideration of the applicable RGs, including RG 8.8, as part of the ALARA design criteria. The following paragraphs describe examples of using ALARA principles in design.

1.2.2.2 Equipment Design Considerations to Limit Time Spent in Radiation Areas Equipment instrumentation and controls are located in accessible areas.

Equipment is selected to minimize potential dose to personnel during maintenance. The selected equipment provides drainage capabilities to facilitate maintenance activities and smooth surfaces to reduce potential for contamination and facilitate decontamination efforts. Selection of components includes consideration for high reliability, ease of decontamination, maintenance and replacement, and accessibility. When possible, components cale US460 SDAA 12.1-2 Revision 1

  • radiation-damage-resistant materials in high-radiation areas to reduce the need for frequent replacement and to reduce the probability of contamination from leakage.
  • stainless steel for constructing or lining components, where it is compatible with the process, to reduce corrosion and provide options for decontamination methods.
  • adequate working space for easy accessibility.
  • locating valves in areas separated from potentially radioactive components.
  • straight-through valve configurations to facilitate maintenance and avoid the buildup of accumulations in internal crevices.

Section 12.1.3 provides site-specific information describing how the plant implements the design consideration guidance in RG 8.8.

1.2.2.3 Equipment Design Considerations to Limit Component Radiation Levels Equipment design considerations directed toward minimizing radiation levels near equipment or components requiring personnel attention include the following:

  • The materials selected for components are chosen to meet service requirements and minimize cobalt-containing materials (e.g., Stellite) coming in contact with the primary coolant system.
  • The design minimizes, to the extent possible, cobalt or nickel-containing alloys for the material to reduce the production of cobalt-60 and cobalt-58.
  • Equipment is designed with provisions to limit leaks, and the plant is designed to collect and control leaked fluid by using sumps and drip pans piped to floor drains that are routed to the liquid radioactive waste system.
  • Components requiring periodic servicing or maintenance are separated, when possible, from highly radioactive sources.
  • Piping design avoids the creation of stagnant legs, uses sloping pipe runs, and locates connections above the pipe centerline.
  • Crud deposition within the primary coolant system is reduced by smooth surfaces that minimize crud traps.
  • The liquid radioactive waste system is provided with a clean-in-place skid that allows flushing system components with demineralized water, as needed.

1.2.2.4 Water Chemistry Reactor coolant water chemistry is controlled during operation to minimize corrosion of surfaces in contact with the coolant and minimize the production cale US460 SDAA 12.1-3 Revision 1

1.2.3 Facility Layout General Design Considerations for Maintaining Radiation Exposures as Low as Reasonably Achievable The design utilizes operating experience and lessons learned from past plant designs to provide an efficient layout that provides reduced personnel exposures.

The radiation protection support facilities are located in the Radioactive Waste Building and include change rooms, offices, calibration facilities, counting room, hot machine shop, and equipment and personnel decontamination facilities. The Radioactive Waste Building also serves as the access portal to the radiologically controlled area, and includes dosimetry issue and personnel contamination monitors.

1.2.3.1 Minimizing Personnel Time Spent in Radiation Areas Facility design considerations used in minimizing personnel time spent in radiation areas include

  • space within cubicles for a laydown area for special tools and ease of servicing activities.
  • instrumentation readouts, monitors, and control points located in low radiation zones.
  • provisions for removing components and transporting them to low radiation zones where shielding and special tools are available.
  • use of reach rods and remote operators for valves in high-radiation areas.

1.2.3.2 Minimizing Radiation Levels in Plant Access Areas and Vicinity of Equipment Facility general design considerations directed toward minimizing radiation levels in plant access areas and in the vicinity of equipment requiring personnel attention include the following:

  • shielding between components.
  • labyrinth entrances to reduce radiation streaming out of cubicle entrances.
  • shield wall penetrations configurations to prevent "line-of-sight" streaming.
  • pipe chases for pipes containing significant radioactive material.
  • radiation areas where station personnel spend substantial time are designed to the lowest practical dose rates.
  • curbing and sloped floors direct leakage to local drains or sumps to limit the spread of contamination from liquid systems.
  • tanks containing radioactive liquids are designed with sloped bottoms toward outlets and flushing or cleaning features.

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  • pumps chosen to minimize leakage and provide housing drains.
  • radiation sources are separated from occupied areas where practicable (e.g., pipes or ducts containing high radioactive fluids not passing through occupied areas).
  • when permanent shielding is impractical, provisions for temporary shielding.
  • instrumentation designed, selected, and located with consideration for long service life, ease and low frequency of calibration, and low crud accumulation.
  • provisions to permit the rapid manipulation of shielding and insulation for equipment that requires periodic inspection or service.
  • adequate space for moveable or temporary shielding for sources.
  • means to control contamination and to facilitate decontamination of potentially contaminated areas.
  • piping for "clean services" (e.g., station air, potable water, nitrogen) is located separate from piping for contaminated systems to avoid cross-contamination.
  • features that permit remote removal, installation, inspection, or servicing of radioactive components.
  • design features such as ventilation isolation or filtration and heating ventilation and air conditioning design such that air flows from areas of lower radioactivity to areas of higher radioactivity to protect against airborne contamination.

1.3 Operational Considerations L Item 12.1-1: An applicant that references the NuScale Power Plant US460 standard design will describe the operational program to maintain exposures to ionizing radiation as far below the dose limits as practical, as low as reasonably achievable (ALARA).

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This section describes the sources of both contained and airborne radiation that provide input to:

  • radiation shielding design calculations.
  • ventilation systems design.
  • radiation protection assessment, including personnel protection.

2.1 Contained Sources The contained radiation sources are developed for normal operation and shutdown conditions. The design basis primary coolant activity concentrations (Section 11.1) are the basis for the contained radiation sources. They are determined by propagating this radionuclide activity through various plant systems using the parameters and assumptions provided in this section. In order for the radiological source terms to be used in shielding calculations, the isotopic inventory is used to calculate the intensity and energy spectrum of the total emitted radiation. The ORIGEN-S code is used to bin the particle emissions into default energy bins based on the activity of each individual isotope. This section describes the radiation sources that provide part of the basis for the design of radiation shielding features. The radiation zone maps in Section 12.3 include drawings showing locations of contained sources.

2.1.1 Reactor Core During normal reactor operations, neutron and gamma radiation are released from the reactor core and from the primary coolant. This radiation is attenuated by the reactor internals, the reactor vessel, the containment vessel, the water surrounding the NuScale Power Module (NPM), the reactor pool concrete walls, and by the bioshield. Table 12.2-1 provides the fission neutron source strength as well as neutron energy spectrum information. The n-gamma and fission gamma source strength is internally generated by MCNP6 using the neutron source strength as an input. The fission neutron source utilizes the Watt spectrum for U-235.

2.1.2 Reactor Coolant System Radionuclides present in the reactor coolant system (RCS) are generated from the release of radioactive materials from postulated fuel clad defects and neutron activation of the primary coolant and impurities in the primary coolant.

The contribution of gamma radiation from the primary coolant is comprised of two components: the primary coolant at the steam generator entrance and at the core exit. The nitrogen-16 concentration is calculated at the core exit, the top of the upper riser/steam generator entrance, and at various points along the chemical and volume control system (CVCS) letdown line. Because of the low flow velocity cale US460 SDAA 12.2-1 Revision 1

corrosion and wear activation products (commonly referred to as CRUD) are uniformly modeled on a primary coolant mass basis. Tables 12.2-2 and 12.2-3 provide the primary coolant gamma spectra. Table 12.2-4 tabulates the nitrogen-16 concentration at several locations.

2.1.3 Chemical and Volume Control System The CVCS processes a portion of the RCS through heat exchangers, demineralizers, and filters. The treated primary coolant is then returned to the RCS (Section 9.3.4). During this treatment process, components of the CVCS can become radiation sources due to soluble and non-soluble radionuclides in the primary coolant. The CVCS contained sources are determined using the design basis coolant source term from Section 11.1 (Table 11.1-4).

Mixed-Bed and Cation Bed Demineralizers The CVCS mixed-bed demineralizers are modeled in continuous operation during the entire fuel cycle. The decontamination factors assumed are listed in Table 11.1-2.

The CVCS cation bed demineralizers are modeled in operation for one-half of the fuel cycle because they are operated intermittently during the operating cycle for lithium removal. Table 12.2-5 lists the assumed decontamination factors.

Tables 12.2-6 and 12.2-7 list the mixed-bed source terms and source strengths, respectively. These source terms and the associated analyses do not include short-term transients such as CRUD bursts associated with refueling outages.

This results in the estimates of activity within some plant structures, systems, and components to not reflect the CRUD-burst related activity, including the CVCS mixed-bed demineralizer values (both columns) in Table 12.2-6 and Table 12.2-7.

It is estimated that a CRUD burst could add up to 680 curies of CRUD isotopes to the CVCS mixed-bed demineralizer.

Regenerative and Non-Regenerative Heat Exchangers The CVCS regenerative and non-regenerative heat exchangers are shell and tube type, as described in Section 9.3.4. To calculate the radiological source term, the heat exchangers are assumed to be completely filled with primary coolant. The major source term model assumptions are listed in Table 12.2-5. The source term for the RCS water is found in Table 11.1-4.

Module Heatup System Heater The module heatup system heater is modeled with 100 percent design basis primary coolant using the parameters listed in Table 12.2-5.

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A generic resin transfer line is modeled assuming it is 100 percent obstructed by resin beads from the CVCS mixed-bed demineralizer using a bulk dry resin density. Table 12.2-5 lists the parameters for modeled the generic resin transfer lines. The source term used for the spent resin transfer line is the CVCS mixed-bed demineralizer decayed for 48 hours5.555556e-4 days <br />0.0133 hours <br />7.936508e-5 weeks <br />1.8264e-5 months <br />, as provided in Table 12.2-6 and Table 12.2-7.

Reactor Coolant Filters The reactor coolant filters are cartridge filters located downstream of the ion exchangers that clean the primary coolant in the CVCS and are modeled to remove CRUD particulate. Table 12.2-5 lists the assumed filter efficiency.

Tables 12.2-6 and 12.2-7 list the filter source term and source strength, respectively.

2.1.4 Pool Cooling and Cleanup System During normal conditions of operation, the pool cooling and cleanup system (PCWS) provides for water level control and temperature maintenance of the reactor pool, the refueling pool and the spent fuel pool. It also removes impurities to reduce radiation exposures and to maintain water chemistry and clarity.

Section 9.1.3 further describes these system.

The pool cooling heat exchangers are conservatively assumed to be filled with reactor pool water even though the shell side is normally filled with site cooling water. Because the majority of the radioactivity consists of tritium, these heat exchangers do not represent a significant radiation source that requires radiation shielding. The PCWS demineralizers are assumed to collect the entire inventory of cleanable radioisotopes in the pool water as shown in Table 12.2-9. It is also assumed the PCWS demineralizers operate for two years, collecting the entire reactor pool water radionuclide inventory eight times (assuming a plant with 6 NPMs on an 18-month refueling cycle). The PCWS filters are assumed to collect CRUD particulates and are operated for one year.

Table 12.2-8 lists the input assumptions used to develop source terms.

Tables 12.2-9 and 12.2-10 provide the radionuclide source terms and source strengths respectively, for the equipment.

2.1.5 Liquid Radioactive Waste System The radionuclide inventory in the liquid radioactive waste system (LRWS) includes fission and activation products originating from the reactor core and the RCS.

Table 11.2-3 lists the estimated input flows from various sources to the high-conductivity waste (HCW) collection tanks, and the low-conductivity waste (LCW) collection tanks. These inputs are processed in batches by the liquid radioactive waste processing skids and sent to the HCW and LCW sample tanks for final disposition. Table 12.2-11 lists the assumed values for the LRW processing equipment radionuclide collection efficiencies and geometries.

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2.1.6 Gaseous Radioactive Waste System The radionuclide input to the gaseous radioactive waste system (GRWS) comes primarily from the LRWS degasifier, which strips the dissolved gases from the primary coolant that enters the degasifier from the CVCS. The gases from the degasifier are sent to the GRWS for conditioning and processing. Table 12.2-14 lists the assumed values pertaining to the GRWS source geometries and Table 11.3-1 describes the GRWS processing parameters. Tables 12.2-15 and 12.2-16 respectively, provide the GRWS component source terms and strengths.

The radioisotopic inventory shown in Table 12.2-15 for the GRWS guard bed and decay beds results in a lesser RG 1.143 safety classification than what is shown in Table 11.3-2. Because an end of operating cycle degasification evolution could result in a transient radioisotopic inventory that exceeds RW-IIb, the classification of the guard bed and decay beds are increased to RW-IIa to cover such transients, as reflected in Table 11.3-2.

2.1.7 Solid Radioactive Waste System Table 12.2-17 lists the assumed values used to develop the solid radioactive waste system (SRWS) component sources modeling in shielding analysis.

Table 12.2-18 lists the radionuclide inventory of the major SRWS components and Table 12.2-19 lists the SRWS component source strengths. For shielding design purposes, it is assumed that the Class A/B/C high integrity container (HIC) storage area contains five HICs loaded with Class B/C dewatered spent resins from the spent resin storage tank, which is decayed for approximately two years.

Table 12.2-12b provides the radionuclide inventory of the drum dryer and Table 12.2-13b provides the drum dryer source strength. Storage areas are shielded to limit the radiation level to be compliant with the designated radiation zone.

2.1.8 Reactor Pool Water There are two sources of radioactive material considered for the reactor pool water: primary coolant released during refueling outages and direct neutron activation. Because of the low power and low temperatures in the spent fuel pool, the radionuclide contribution to the pool water from defective fuel assemblies in the storage racks is considered negligible. The primary source of radionuclides in the reactor pool comes from the primary coolant system when an NPM is disassembled in the reactor pool during outages. During refueling outages, after the primary coolant is cleaned by the CVCS, the remaining quantities of radionuclides are released into the pool water during NPM disassembly. The post-CRUD burst cleanup of the primary coolant in the NPM by CVCS operates until the projected dose rate (after NPM disassembly) to an operator on the refueling bridge is less than 2.5 mrem/hr. Table 12.2-8 lists the major input assumptions for the pool water source term and PCWS component shielding modeling.

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water. The neutron flux at the outside edge of the containment vessel is many orders of magnitude less than the average neutron flux in the core and continues to decrease in the reactor pool borated water. The amount of neutron activation products in the reactor pool water is determined to be insignificant compared to the amount of primary coolant radionuclides released to the reactor pool water during refueling outages.

Table 12.2-8 lists the characteristics of the pool surge control storage tank, which is modeled as a vertical cylinder.

Tables 12.2-9 and 12.2-10 provide the source terms and source strengths respectively, for the pool water and pool surge control storage tank.

2.1.9 Spent Fuel Spent fuel stored in the spent fuel racks presents a radiation source that is shielded by the water in the spent fuel pool as well as by the pool walls. The same methodology used to determine the maximum core isotopic source term in Section 11.1 is used to develop the spent fuel source term, resulting in the bounding assumption that the spent fuel racks are filled with irradiated fuel assemblies. Spent fuel gamma ray and neutron source strengths are considered in the evaluation of radiation levels for fuel handling and spent fuel storage.

Spent fuel gamma ray source strengths are presented in Table 12.2-20 for a spent fuel rack full of irradiated fuel assemblies. Spent fuel neutron source strengths are given in Table 12.2-21 for the same spent fuel rack.

2.1.10 In-Core Instruments There are 12 fuel assemblies distributed in the reactor core that are instrumented with in-core instruments. Each of the 12 instruments contains self-powered neutron detectors and thermocouples. During reactor operations, the in-core instruments are irradiated, resulting in activation. Table 12.2-22 lists the major input assumptions and Table 12.2-23 provides the gamma spectra.

2.1.11 Control Rods and Secondary Source Rods Control Rod Assemblies Because the reactor core operates in an all-rods-out configuration, it is assumed that only the tip of the control rod is irradiated. This portion of the control rod assembly (CRA) consists of Ag-In-Cd neutron absorber. Table 12.2-24 lists the major input assumptions and Table 12.2-25 lists the CRA gamma spectra. The activated source from the CRA tips peaks early, therefore the source term reported is for end of Cycle 1.

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The secondary source is antimony and beryllium (Sb-Be) and is irradiated for 40 cycles. Flux is the same as for the in-core instruments (Section 12.2.1.10).

Table 12.2-26 lists the gamma ray source strengths associated with the secondary source rods.

2.1.12 Secondary Coolant System Primary-to-secondary leaks through the steam generator can introduce primary coolant activity into the secondary system with the resultant contamination level being dependent on the activity level in the primary coolant and the magnitude of the steam generator leak. Because the condensate polishing system is a full-flow system, the condensate polishers are evaluated for the radioactive material that could accumulate on the resins during the period between resin regenerations.

Assuming the secondary coolant is at the design basis concentrations (Table 11.1-5), resin decontamination factors consistent with NUREG-0017, and a 10-day resin regeneration period, the accumulation of radioactive material is less than 100 mCi. The model excludes tritium from this activity because tritium does not accumulate on the resin.

2.1.13 Post-Accident Sources The iodine spike design basis source term (Section 15.0.3 describes the maximum primary coolant activity released from the design bases accidents) is evaluated for equipment qualification (EQ) in and around an NPM. Three volumes associated with the NPM are modeled for design basis accident EQ dose consequences from a design basis accident: the reactor pressure vessel and containment vessel combined liquid sump volume, the containment vapor volume, and the bioshield envelope volume. The iodine spike design basis source term maximum post-accident activity concentrations used for EQ evaluation are provided on a mass basis in Table 12.2-31. The specific concentration values in Table 12.2-31 are in excess of the values that would be calculated using the methodology in TR-0915-17565-P-A (Reference 12.2-4), with the design inputs provided in Chapter 11 and Chapter 12. Plateout of activity onto containment surfaces is neglected due to the small containment volume and the lack of surface coatings inside containment. There is also no aerosol removal assumed. Other assumptions for the post-accident EQ source term are listed in Table 12.2-27. The three volumes are evaluated with conservative assumptions, including instantaneous and homogeneous releases into the volume of interest.

Table 12.2-28 lists the integrated post-accident source energy deposition versus time for both photons and electrons for the three evaluated volumes.

Table 12.2-28 also tabulates the integrated doses for various times post-accident.

Section 3.11 and Appendix 3C contain additional details on EQ. Consistent with 10 CFR 50.34(f)(2)(vii), areas that could contain core damage post-accident sources are evaluated for equipment protection. Section 19.2 addresses equipment protection from a core damage source term.

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There are no other identified contained sources that exceed 100 mCi.

L Item 12.2-1: An applicant that references the NuScale Power Plant US460 standard design will describe additional site-specific contained radiation sources that exceed 100 millicuries (including sources for instrumentation and radiography) not identified in Section 12.2.1.

2.2 Airborne Radioactive Material Sources This section describes the airborne radioactive material sources that form part of the basis for design of ventilation systems and personnel protective measures, and also are considered in personnel dose assessment.

2.2.1 Reactor Building Atmosphere Airborne radioactivity may be present in the reactor building (RXB) atmosphere due to reactor pool evaporation or primary coolant leakage. The airborne concentration is modeled as a buildup to an equilibrium concentration given the production rate and removal rate, and on an evaporation rate calculated following the model in the Heating, Ventilating, and Air-conditioning Applications Handbook (Reference 12.2-3). The concentration of tritium in the reactor pool water is developed assuming the primary coolant letdown is recycled to the reactor pool.

The concentration of tritium in the primary coolant leakage is developed assuming the primary coolant letdown is recycled back to the RCS. Each case maximizes the tritium concentration in the fluid of interest using the concentrations in Table 11.1-8. The airborne concentration in the air space above the reactor pool is determined by using the peak reactor pool water source term. Table 12.2-29 lists the input parameters.

A ( ) = ( C pool x p f x F evap ) ( + ( F air V air ) )

where, A ( ) = equilibrium airborne concentration, Cpool = pool water concentration, pf = partition fraction,

= decay constant, Fair/Vair = air change rate, and Fevap = pool evaporation rate = A/Y(pw-pa)(95+0.425V),

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A = area of pool surface, ft2 Y = Latent heat of evaporation at surface water temperature, Btu/lb pw = saturation vapor pressure at surface water temperature, in. Hg pa = saturation vapor pressure at room air dew point, in. Hg V = air velocity of water surface, fpm.

Primary coolant leaks can occur in the RXB from the CVCS. In areas that are routinely occupied, the RXB heating ventilation and air conditioning system provides sufficient air flow to maintain airborne concentrations to acceptable levels where CVCS leaks are a potential. The airborne concentrations in the RXB cubicles are determined using the same equilibrium model as the reactor pool area, but using CVCS leaks for the production term.

A ( ) = ( PCA x p leak x p f x F leak ) ( + ( F air /V air ) )

where, A ( ) = equilibrium airborne concentration, PCA = primary coolant activity concentration, pleak = leak flashing fraction, pf = partition fraction, Fleak = primary coolant leak rate,

= radioactive decay constant, and Fair/Vair = air change rate.

Table 12.2-30 lists the resultant airborne isotopic concentration in the RXB atmosphere. Section 12.3.4 describes monitoring airborne radioactivity within the air spaces of the facility. Section 11.5 describes monitoring gaseous effluents.

2.2.2 Turbine Building Atmosphere Section 12.2.1.12 considers the secondary coolant to be clean for normal operating conditions. Therefore, the Turbine Building atmosphere contains minimal airborne radioactive material.

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12.2-1 International Atomic Energy Agency, "Combined Methods for Liquid Radioactive Waste Treatment," IAEA-TECDOC-1336, Vienna, Austria, February 2003.

12.2-2 Electric Power Research Institute, "Pressurized Water Reactor Primary Water Chemistry Guidelines," Vols. 1 and 2, EPRI #3002000505, EPRI, Palo Alto, CA, 2014.

12.2-3 American Society of Heating, Refrigerating and Air-Conditioning Engineers (ASHRAE), Handbook: Heating, Ventilating, and Air-conditioning Applications," Atlanta, GA, 2007.

12.2-4 NuScale Power, LLC, "Accident Source Term Methodology,"

TR-0915-17565-P-A, Revision 4.

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Parameter Value Units ion Neutron Source Strength 2.6E+19 Particles/s ion Neutron Energy Spectrum U-235 -

l Primary Coolant Source Strength 1.6E+14 Particles/s cale US460 SDAA 12.2-10 Revision 1

Gamma Source Term Energy Group Energy (MeV) Gamma Source Lower Bound Upper Bound (photons/sec/gram primary coolant) 1 1.00E-02 2.00E-02 8.9E+04 2 2.00E-02 3.00E-02 5.5E+04 3 3.00E-02 4.50E-02 1.8E+05 4 4.50E-02 6.00E-02 3.3E+04 5 6.00E-02 7.00E-02 1.7E+04 6 7.00E-02 7.50E-02 7.2E+03 7 7.50E-02 1.00E-01 1.4E+05 8 1.00E-01 1.50E-01 3.5E+04 9 1.50E-01 2.00E-01 2.8E+04 10 2.00E-01 2.60E-01 2.5E+04 11 2.60E-01 3.00E-01 8.1E+03 12 3.00E-01 4.00E-01 2.3E+04 13 4.00E-01 4.50E-01 8.2E+03 14 4.50E-01 5.10E-01 8.5E+03 15 5.10E-01 5.12E-01 5.4E+02 16 5.12E-01 6.00E-01 7.8E+03 17 6.00E-01 7.00E-01 1.0E+04 18 7.00E-01 8.00E-01 7.6E+03 19 8.00E-01 9.00E-01 6.1E+03 20 9.00E-01 1.00E+00 3.8E+03 21 1.00E+00 1.20E+00 6.4E+03 22 1.20E+00 1.33E+00 1.2E+04 23 1.33E+00 1.44E+00 2.8E+03 24 1.44E+00 1.50E+00 8.5E+02 25 1.50E+00 1.57E+00 9.4E+02 26 1.57E+00 1.66E+00 1.2E+03 27 1.66E+00 1.80E+00 3.8E+03 28 1.80E+00 2.00E+00 3.2E+03 29 2.00E+00 2.15E+00 1.1E+03 30 2.15E+00 2.35E+00 4.7E+02 31 2.35E+00 2.50E+00 2.7E+03 32 2.50E+00 2.75E+00 1.4E+04 33 2.75E+00 3.00E+00 3.5E+03 34 3.00E+00 3.50E+00 9.0E+02 35 3.50E+00 4.00E+00 1.0E+03 36 4.00E+00 4.50E+00 3.7E+02 37 4.50E+00 5.00E+00 3.4E+02 38 5.00E+00 5.50E+00 3.1E+02 39 5.50E+00 6.00E+00 1.5E+02 40 6.00E+00 6.50E+00 1.0E+06 41 6.50E+00 7.00E+00 6.6E+02 42 7.00E+00 7.50E+00 7.3E+04 43 7.50E+00 8.00E+00 2.1E+01 44 8.00E+00 1.00E+01 1.2E+03 cale US460 SDAA 12.2-11 Revision 1

Energy Group Energy (MeV) Gamma Source Lower Bound Upper Bound (photons/sec/gram primary coolant) 45 1.00E+01 1.20E+01 3.0E-01 46 1.20E+01 1.40E+01 0.0E+00 47 1.40E+01 2.00E+01 0.0E+00 Total 1.8E+06 cale US460 SDAA 12.2-12 Revision 1

Energy Group Energy (MeV) DB PCA Core Exit N-16 Lower Bound Upper Bound (/s/g) 1 1.00E-02 2.00E-02 4.1E+05 2 2.00E-02 3.00E-02 2.4E+05 3 3.00E-02 4.50E-02 3.3E+05 4 4.50E-02 6.00E-02 1.6E+05 5 6.00E-02 7.00E-02 7.7E+04 6 7.00E-02 7.50E-02 3.4E+04 7 7.50E-02 1.00E-01 2.6E+05 8 1.00E-01 1.50E-01 1.6E+05 9 1.50E-01 2.00E-01 1.3E+05 10 2.00E-01 2.60E-01 8.4E+04 11 2.60E-01 3.00E-01 3.7E+04 12 3.00E-01 4.00E-01 1.0E+05 13 4.00E-01 4.50E-01 3.6E+04 14 4.50E-01 5.10E-01 3.9E+04 15 5.10E-01 5.12E-01 5.4E+02 16 5.12E-01 6.00E-01 2.3E+04 17 6.00E-01 7.00E-01 3.5E+04 18 7.00E-01 8.00E-01 2.7E+04 19 8.00E-01 9.00E-01 2.1E+04 20 9.00E-01 1.00E+00 1.6E+04 21 1.00E+00 1.20E+00 2.5E+04 22 1.20E+00 1.33E+00 2.2E+04 23 1.33E+00 1.44E+00 8.5E+03 24 1.44E+00 1.50E+00 3.3E+03 25 1.50E+00 1.57E+00 3.3E+03 26 1.57E+00 1.66E+00 5.4E+03 27 1.66E+00 1.80E+00 1.6E+04 28 1.80E+00 2.00E+00 1.3E+04 29 2.00E+00 2.15E+00 4.2E+03 30 2.15E+00 2.35E+00 4.7E+02 31 2.35E+00 2.50E+00 1.0E+04 32 2.50E+00 2.75E+00 6.2E+04 33 2.75E+00 3.00E+00 1.6E+04 34 3.00E+00 3.50E+00 4.2E+03 35 3.50E+00 4.00E+00 4.8E+03 36 4.00E+00 4.50E+00 1.7E+03 37 4.50E+00 5.00E+00 1.6E+03 38 5.00E+00 5.50E+00 1.5E+03 39 5.50E+00 6.00E+00 7.2E+02 40 6.00E+00 6.50E+00 4.7E+06 41 6.50E+00 7.00E+00 3.1E+03 42 7.00E+00 7.50E+00 3.5E+05 43 7.50E+00 8.00E+00 9.9E+01 44 8.00E+00 1.00E+01 5.5E+03 45 1.00E+01 1.20E+01 1.4E+00 46 1.20E+01 1.40E+01 0.0E+00 cale US460 SDAA 12.2-13 Revision 1

Energy Group Energy (MeV) DB PCA Core Exit N-16 Lower Bound Upper Bound (/s/g) 47 1.40E+01 2.00E+01 0.0E+00 Total 7.5E+06 cale US460 SDAA 12.2-14 Revision 1

Primary Coolant Location µCi/g e exit 2.0E+02 of upper riser / entrance to SG 4.1E+01 S letdown line 2.4E+00 S heat exchanger 7.7E-01 cale US460 SDAA 12.2-15 Revision 1

Assumptions Model Parameter Value S mixed bed: -

VCS mixed bed operation time 2 years econtamination Factors Table 11.1-2 eometry Vertical Cylinder Source dimensions of vessel diameter=21.6 in, Height=95 in Shielding thickness of steel shell 1.22 in S Cation bed: -

VCS Cation Bed Operation Time 1 year VCS Cation Bed Decontamination Factors: -

Halogens 1 Cs, Rb 10 Others 10 eometry Vertical Cylinder Source dimensions of vessel diameter=21.6 in, Height=95 in Shielding thickness of steel shell 1.22 in enerative and Non-Regenerative Heat Exchangers: -

ontents 100% Primary Coolant eometry -

Regenerative heat exchanger 3x2 array of horizontal Cylinders Source dimensions of each cylinder diameter=12.8 in, Height=98.8 in Shielding thickness of steel shell 1.6 in Non-Regenerative heat exchanger 1x2 array of horizontal Cylinders Source dimensions of each cylinder diameter=11.5 in, Height=66.5 in Shielding thickness of steel shell 1.25 in ule Heating System Heater: -

ontents 100% Primary Coolant No-N16 eometry Horizontal Cylinder Source dimensions diameter=20.4 in, Height=142.4 in Shielding thickness of steel shell 1.81 in S flowrate 180 lbm/min S filter efficiency 9.1% (DF 1.1) eometry Vertical Cylinder Dimensions diameter=10.1 in, Height= 65 in Shielding thickness of steel shell 1.31 in S resin transfer line: -

pe internal diameter 1.69 in pe wall thickness 0.344 in pe length 36.4 ft esin source term CVCS MB Resin (48 hr Decay)

S pipe inside vertical pipe chase -

ontents 100% Primary Coolant with N-16 concentration of CVCS letdown line.

eometry Vertical Cylinder Source length of pipe 43.5 ft Shielding dimensions of pipe diameter=2.13 in, Thickness= 0.375 in cale US460 SDAA 12.2-16 Revision 1

Radionuclide Content CVCS Mixed Bed CVCS Particulate CVCS Mixed Bed IX CVCS Cation Bed IX Transferred - 48 hour5.555556e-4 days <br />0.0133 hours <br />7.936508e-5 weeks <br />1.8264e-5 months <br /> Radionuclide Filter decay (Ci) (Ci) (Ci) (Ci)

Kr-83m 2.1E-02 - - 2.0E-08 Kr-85m 2.3E-05 - - 3.5E-09 Kr-85 6.2E-09 - - 1.6E-09 Kr-87 - - - -

Kr-88 - - - -

Kr-89 - - - -

Xe-131m 7.0E-01 - - 1.7E-01 Xe-133m 2.8E-01 - - 5.3E-02 Xe-133 9.5E+00 - - 2.1E+00 Xe-135m 3.2E-01 - - 5.3E-04 Xe-135 1.6E+00 - - 3.2E-02 Xe-137 - - - -

Xe-138 - - - -

Br-82 5.3E-02 - - 5.1E-03 Br-83 2.1E-02 - - 4.9E-09 Br-84 2.1E-03 - - 2.9E-31 Br-85 2.3E-05 - - -

I-129 3.0E-04 1.4E-10 - 7.5E-05 I-130 1.5E-01 - - 2.6E-03 I-131 6.0E+01 9.4E-04 - 1.3E+01 I-132 2.8E+00 2.2E-02 - 4.1E-01 I-133 9.8E+00 1.9E-05 - 5.0E-01 I-134 7.7E-02 2.5E-05 - 6.7E-19 I-135 2.0E+00 - - 3.1E-03 Rb-86m 3.1E-09 1.4E-09 - -

Rb-86 4.8E-01 2.1E-01 - 1.1E-01 Rb-88 5.4E-02 2.4E-02 - 2.3E-51 Rb-89 2.1E-03 9.5E-04 - 3.1E-61 Cs-132 3.3E-03 1.5E-03 - 6.7E-04 Cs-134 1.4E+03 3.5E+02 - 3.4E+02 Cs-135m 1.1E-04 5.0E-05 - 1.2E-21 Cs-136 1.0E+01 4.7E+00 - 2.4E+00 Cs-137 9.3E+02 2.1E+02 - 2.3E+02 Cs-138 3.8E-02 1.7E-02 - 1.1E-28 P-32 2.0E-06 1.8E-08 - 4.5E-07 Co-57 2.4E-07 1.6E-09 - 6.1E-08 Sr-89 3.2E-01 3.9E-03 - 7.8E-02 Sr-90 4.9E-01 2.3E-03 - 1.2E-01 Sr-91 1.3E-03 1.2E-05 - 1.0E-05 Sr-92 2.0E-04 1.8E-06 - 1.8E-10 Y-90 4.9E-01 2.3E-03 - 1.2E-01 Y-91m 8.3E-04 7.7E-06 - 6.7E-06 Y-91 5.5E-02 5.0E-04 - 1.3E-02 cale US460 SDAA 12.2-17 Revision 1

CVCS Mixed Bed CVCS Particulate CVCS Mixed Bed IX CVCS Cation Bed IX Transferred - 48 hour5.555556e-4 days <br />0.0133 hours <br />7.936508e-5 weeks <br />1.8264e-5 months <br /> Radionuclide Filter decay (Ci) (Ci) (Ci) (Ci)

Y-92 4.2E-04 3.9E-06 - 2.0E-08 Y-93 3.0E-04 2.8E-06 - 2.9E-06 Zr-97 7.3E-04 6.7E-06 - 2.5E-05 Nb-95 1.1E+00 9.5E-03 - 1.0E+00 Mo-99 5.2E+00 4.8E-02 - 7.8E-01 Mo-101 7.3E-04 6.7E-06 - 8.4E-64 Tc-99m 5.0E+00 4.6E-02 - 7.6E-01 Tc-99 1.8E-02 8.3E-05 - 4.5E-03 Ru-103 7.1E-02 6.5E-04 - 1.7E-02 Ru-105 1.1E-04 1.0E-06 - 1.5E-08 Ru-106 3.1E-01 1.9E-03 - 7.8E-02 Rh-103m 7.0E-02 6.4E-04 - 1.7E-02 Rh-105 1.9E-03 1.8E-05 - 1.9E-04 Rh-106 3.1E-01 1.9E-03 - 7.8E-02 Ag-110 1.6E-01 1.1E-03 - 1.6E-01 Sb-124 1.6E-04 1.5E-06 - 4.0E-05 Sb-125 8.0E-03 4.1E-05 - 2.0E-03 Sb-127 3.9E-04 3.6E-06 - 6.8E-05 Sb-129 2.3E-05 2.1E-07 - 3.0E-09 Te-125m 1.7E-01 1.5E-03 - 4.1E-02 Te-127m 1.2E+00 1.0E-02 - 2.9E-01 Te-127 1.2E+00 9.9E-03 - 2.9E-01 Te-129m 1.1E+00 9.8E-03 - 2.6E-01 Te-129 6.7E-01 6.2E-03 - 1.6E-01 Te-131m 1.3E-01 1.2E-03 - 1.1E-02 Te-131 3.0E-02 2.7E-04 - 2.4E-03 Te-132 2.4E+00 2.2E-02 - 3.9E-01 Te-133m 2.5E-03 2.3E-05 - 1.4E-19 Te-134 2.7E-03 2.5E-05 - 1.2E-24 Ba-137m 8.8E+02 2.0E+02 - 2.2E+02 Ba-139 9.9E-05 9.1E-07 - 9.1E-16 Ba-140 1.2E-01 1.1E-03 - 2.7E-02 La-140 1.2E-01 1.1E-03 - 2.9E-02 La-141 8.7E-05 8.0E-07 - 4.5E-09 La-142 1.6E-05 1.5E-07 - 1.2E-15 Ce-141 4.7E-02 4.3E-04 - 1.1E-02 Ce-143 1.5E-03 1.4E-05 - 1.4E-04 Ce-144 2.9E-01 1.9E-03 - 7.1E-02 Pr-143 1.9E-02 1.7E-04 - 4.2E-03 Pr-144 2.8E-01 1.8E-03 - 7.1E-02 Np-239 5.4E-02 4.9E-04 - 7.4E-03 Na-24 1.4E+00 1.3E-02 2.6E-03 1.6E-01 Cr-51 3.6E+00 3.3E-02 6.6E-03 3.4E+00 cale US460 SDAA 12.2-18 Revision 1

CVCS Mixed Bed CVCS Particulate CVCS Mixed Bed IX CVCS Cation Bed IX Transferred - 48 hour5.555556e-4 days <br />0.0133 hours <br />7.936508e-5 weeks <br />1.8264e-5 months <br /> Radionuclide Filter decay (Ci) (Ci) (Ci) (Ci)

Mn-54 1.7E+01 1.1E-01 2.1E-02 1.6E+01 Fe-55 2.0E+01 1.0E-01 2.1E-02 2.0E+01 Fe-59 5.5E-01 5.1E-03 1.0E-03 5.4E-01 Co-58 1.3E+01 1.2E-01 2.4E-02 1.3E+01 Co-60 9.7E+00 4.8E-02 9.6E-03 9.7E+00 Ni-63 5.5E+00 2.5E-02 5.1E-03 5.5E+00 Zn-65 4.5E+00 3.0E-02 6.2E-03 4.5E+00 Zr-95 1.0E+00 9.3E-03 1.9E-03 1.0E+00 Ag-110m 1.2E+01 7.8E-02 1.6E-02 1.2E+01 W-187 1.2E-01 1.1E-03 2.1E-04 2.8E-02 H-3 - - - -

C-14 - - - -

N-16 - - - -

Ar-41 - - - -

9.0E+02 cale US460 SDAA 12.2-19 Revision 1

Scale Final Safety Analysis Report Source Strengths Design Basis Primary CVCS CVCS Mixed CVCS Letdown Coolant at CVCS Mixed- CVCS Cation Energy (MeV) Particulate Bed Transfer - - 71.3 second CVCS Pipe Bed Bed ergy Group Filter 48 hour5.555556e-4 days <br />0.0133 hours <br />7.936508e-5 weeks <br />1.8264e-5 months <br /> decay decay Chase Photon Spectra N-16 (photon/sec/

Lower Bound Upper Bound photons/sec photons/sec photons/sec photons/sec photons/sec gram) 1 1.00E-02 2.00E-02 7.0E+03 2.7E+11 5.7E+10 4.2E+06 6.5E+10 5.3E+02 2 2.00E-02 3.00E-02 7.5E+03 3.2E+11 3.1E+10 8.5E+06 7.4E+10 1.1E+03 3 3.00E-02 4.50E-02 1.4E+05 2.8E+12 6.0E+11 1.6E+06 6.8E+11 3.4E+04 4 4.50E-02 6.00E-02 2.4E+03 8.0E+10 1.5E+10 1.5E+06 1.9E+10 1.3E+02 5 6.00E-02 7.00E-02 1.2E+03 5.0E+10 1.5E+10 2.3E+06 1.2E+10 6.1E+01 6 7.00E-02 7.50E-02 5.0E+02 1.3E+10 2.9E+09 1.4E+06 3.3E+09 2.4E+01 7 7.50E-02 1.00E-01 1.2E+05 2.4E+11 1.9E+10 8.7E+05 5.5E+10 2.8E+04 8 1.00E-01 1.50E-01 3.2E+03 2.4E+11 1.1E+10 2.8E+06 4.2E+10 2.2E+02 9 1.50E-01 2.00E-01 3.1E+03 1.0E+11 3.2E+10 1.8E+06 2.3E+10 3.9E+02 10 2.00E-01 2.60E-01 1.0E+04 1.7E+11 6.5E+09 1.2E+06 2.1E+10 2.3E+03 11 2.60E-01 3.00E-01 8.0E+02 1.9E+11 2.0E+10 3.6E+05 4.0E+10 3.5E+01 12 3.00E-01 4.00E-01 3.2E+03 2.1E+12 7.6E+10 2.4E+07 4.5E+11 1.1E+02 13 4.00E-01 4.50E-01 1.1E+03 2.9E+10 3.1E+08 2.2E+07 1.7E+10 1.2E+02 14 4.50E-01 5.10E-01 8.7E+02 7.6E+11 1.9E+11 2.4E+06 1.9E+11 4.7E+01 15 5.10E-01 5.12E-01 5.4E+02 1.6E+11 1.4E+09 2.7E+08 1.5E+11 1.2E+02 16 5.12E-01 6.00E-01 4.0E+03 1.2E+13 3.2E+12 7.6E+05 3.0E+12 2.5E+02 17 6.00E-01 7.00E-01 4.1E+03 7.6E+13 1.9E+13 6.8E+08 1.9E+13 2.8E+02 18 7.00E-01 8.00E-01 2.8E+03 4.8E+13 1.3E+13 3.2E+08 1.2E+13 2.0E+02 19 8.00E-01 9.00E-01 2.3E+03 3.9E+12 7.0E+11 2.1E+09 2.0E+12 1.6E+02 20 9.00E-01 1.00E+00 6.4E+02 1.7E+11 1.2E+09 2.0E+08 1.5E+11 3.2E+01 21 1.00E+00 1.20E+00 1.7E+03 2.2E+12 4.9E+11 5.2E+08 8.9E+11 9.9E+01 Radiation Sources 22 1.20E+00 1.33E+00 8.9E+03 3.2E+11 3.5E+10 2.0E+08 2.2E+11 7.9E+03 23 1.33E+00 1.44E+00 1.4E+03 1.8E+12 3.9E+11 4.1E+08 6.6E+11 1.0E+02 24 1.44E+00 1.50E+00 2.2E+02 2.7E+10 1.4E+08 2.5E+07 1.8E+10 3.0E+00 25 1.50E+00 1.57E+00 3.4E+02 6.5E+10 6.3E+08 8.6E+07 6.3E+10 6.4E+01 26 1.57E+00 1.66E+00 1.1E+02 4.8E+09 4.3E+07 1.4E+05 1.1E+09 4.2E+00

Scale Final Safety Analysis Report Design Basis Primary CVCS CVCS Mixed CVCS Letdown Coolant at CVCS Mixed- CVCS Cation Energy (MeV) Particulate Bed Transfer - - 71.3 second CVCS Pipe Bed Bed ergy Group Filter 48 hour5.555556e-4 days <br />0.0133 hours <br />7.936508e-5 weeks <br />1.8264e-5 months <br /> decay decay Chase Photon Spectra N-16 (photon/sec/

Lower Bound Upper Bound photons/sec photons/sec photons/sec photons/sec photons/sec gram) 27 1.66E+00 1.80E+00 6.7E+02 1.9E+10 3.4E+07 4.6E+06 2.6E+09 3.4E+01 28 1.80E+00 2.00E+00 6.5E+02 3.5E+09 2.2E+08 9.9E+04 3.8E+08 6.0E+01 29 2.00E+00 2.15E+00 3.5E+02 1.6E+09 1.6E+07 5.9E+03 1.3E+08 6.7E+01 30 2.15E+00 2.35E+00 4.7E+02 1.2E+09 1.0E+08 4.1E+03 8.5E+07 9.9E+01 31 2.35E+00 2.50E+00 8.0E+02 9.9E+08 3.4E+06 4.4E+00 3.8E+07 1.7E+02 32 2.50E+00 2.75E+00 1.2E+03 2.8E+10 3.3E+08 5.1E+07 3.1E+09 4.4E+01 33 2.75E+00 3.00E+00 4.4E+02 2.5E+10 2.3E+08 4.7E+07 2.7E+09 7.2E+00 34 3.00E+00 3.50E+00 7.0E+01 2.4E+07 7.5E+06 9.0E-02 3.5E+05 3.0E+00 35 3.50E+00 4.00E+00 6.4E+01 4.9E+07 1.6E+06 7.5E+04 4.4E+06 7.7E-01 36 4.00E+00 4.50E+00 2.2E+01 1.3E+06 2.8E+05 8.2E+02 4.8E+04 1.3E-01 37 4.50E+00 5.00E+00 2.3E+01 3.8E+06 1.7E+06 - - 4.9E-01 38 5.00E+00 5.50E+00 1.8E+01 7.1E+03 3.2E+03 - - 6.5E-03 39 5.50E+00 6.00E+00 8.7E+00 - - - - 2.8E-03 40 6.00E+00 6.50E+00 5.7E+04 - - - - 1.8E+01 41 6.50E+00 7.00E+00 3.7E+01 - - - - 1.2E-02 42 7.00E+00 7.50E+00 4.2E+03 - - - - 1.3E+00 43 7.50E+00 8.00E+00 1.2E+00 - - - - 3.8E-04 44 8.00E+00 1.00E+01 6.7E+01 - - - - 2.1E-02 45 1.00E+01 1.20E+01 1.7E-02 - - - - 5.5E-06 46 1.20E+01 1.40E+01 - - - - - -

47 1.40E+01 2.00E+01 - - - - - -

Radiation Sources Total 3.9E+05 1.5E+14 3.7E+13 5.0E+09 4.0E+13 7.7E+04

Assumptions Model Parameter Value l cooling heat exchangers: -

ontents 100% Pool Water ource term mass of each heat exchanger 2.77E+06 g eometry 2x1 array of Horizontal Cylinders Source dimensions of each cylinder diameter=27 in, Height=299 in Shielding thickness of steel shell 0.5 in l cleanup system demineralizer: -

eometry Vertical Cylinder Source dimensions diameter=130 in, Height=98 in Shielding thickness of steel shell 0.25 in peration time 2 years S demineralizer decontamination factors Halogens 100 Cs/Rb 2 Others 50 S filters: -

CWS filter efficiency 9.1%

eometry Horizontal Cylinder Source dimensions diameter=38.9 in, Height=118 in Shielding thickness of steel shell 0.25 in CWS flow rate 164 gpm HS water mass 1.18E+10 grams CWS filter operation time 1 years l Surge Control Tank -

ontents Cleanup Up Pool Water eometry Vertical Cylinder Source dimensions diameter=50 ft, Height=45 ft Shielding thickness of steel wall 0.25 in Source volume 8.8E+04 ft3 Source Mass 2.5E+09 g

Assumes the plant consists of 6 NPMs on an 18-month refueling cycle.

cale US460 SDAA 12.2-22 Revision 1

Radionuclide Content PCWS PCWS Particulate Reactor Pool Water PCWS Surge Tank Radionuclide Demineralizers Filter (Ci) (Ci/g) (Ci/g) (Ci)

Kr-83m 9.6E-13 - - -

Kr-85m - - - -

Kr-85 - - - -

Kr-87 - - - -

Kr-88 - - - -

Kr-89 - - - -

Xe-131m 2.1E-02 - - -

Xe-133m 5.0E-04 - - -

Xe-133 1.7E-02 - - -

Xe-135m 3.6E-07 - - -

Xe-135 1.8E-06 - - -

Xe-137 - - - -

Xe-138 - - - -

Br-82 6.7E-06 2.4E-14 2.4E-16 -

Br-83 9.6E-13 5.2E-20 5.2E-22 -

Br-84 4.5E-38 1.1E-44 1.1E-46 -

Br-85 - - - -

I-129 1.1E-07 1.2E-18 1.2E-20 -

I-130 2.6E-06 2.7E-14 2.7E-16 -

I-131 1.8E+00 1.2E-09 1.2E-11 -

I-132 5.9E-04 9.8E-13 9.8E-15 -

I-133 1.7E-02 1.1E-10 1.1E-12 -

I-134 3.9E-24 5.7E-31 5.7E-33 -

I-135 2.2E-06 4.3E-14 4.3E-16 -

Rb-86m - - - -

Rb-86 1.0E-03 3.1E-13 1.6E-13 -

Rb-88 1.7E-60 7.8E-67 3.9E-67 -

Rb-89 1.4E-71 7.1E-78 3.6E-78 -

Cs-132 6.2E-06 5.3E-15 2.6E-15 -

Cs-134 3.2E+00 4.8E-11 2.4E-11 -

Cs-135m 4.8E-26 7.3E-33 3.6E-33 -

Cs-136 2.2E-02 9.3E-12 4.7E-12 -

Cs-137 2.2E+00 2.5E-11 1.2E-11 -

Cs-138 1.7E-34 4.0E-41 2.0E-41 -

P-32 6.9E-10 2.6E-19 5.2E-21 -

Co-57 9.3E-11 2.2E-21 4.4E-23 -

Sr-89 1.2E-04 1.3E-14 2.6E-16 -

Sr-90 1.9E-04 2.0E-15 4.1E-17 -

Sr-91 9.7E-09 1.3E-16 2.6E-18 -

Sr-92 4.5E-14 2.2E-21 4.4E-23 -

Y-90 1.9E-04 1.2E-15 2.4E-17 -

Y-91m 6.2E-09 8.3E-17 1.7E-18 -

Y-91 2.1E-05 1.9E-15 3.8E-17 -

Y-92 8.1E-12 2.9E-19 5.8E-21 -

cale US460 SDAA 12.2-23 Revision 1

PCWS PCWS Particulate Reactor Pool Water PCWS Surge Tank Radionuclide Demineralizers Filter (Ci) (Ci/g) (Ci/g) (Ci)

Y-93 2.7E-09 3.5E-17 6.9E-19 -

Zr-97 2.9E-08 2.2E-16 4.5E-18 -

Nb-95 3.5E-01 1.4E-12 2.9E-14 -

Mo-99 1.1E-03 2.2E-12 4.4E-14 -

Mo-101 2.9E-75 1.5E-81 3.0E-83 -

Tc-99m 1.1E-03 2.1E-12 4.2E-14 -

Tc-99 7.0E-06 7.4E-17 1.5E-18 -

Ru-103 2.6E-05 3.6E-15 7.1E-17 -

Ru-105 7.9E-12 2.3E-19 4.6E-21 -

Ru-106 1.2E-04 2.3E-15 4.7E-17 -

Rh-103m 2.6E-05 3.5E-15 7.1E-17 -

Rh-105 2.5E-07 9.2E-16 1.8E-17 -

Rh-106 1.2E-04 2.3E-15 4.7E-17 -

Ag-110 5.4E-02 1.5E-12 3.0E-14 -

Sb-124 6.1E-08 5.4E-18 1.1E-19 -

Sb-125 3.1E-06 4.1E-17 8.3E-19 -

Sb-127 9.9E-08 1.4E-16 2.8E-18 -

Sb-129 1.5E-12 4.5E-20 9.0E-22 -

Te-125m 6.3E-05 5.8E-15 1.2E-16 -

Te-127m 4.5E-04 2.2E-14 4.5E-16 -

Te-127 4.4E-04 2.3E-14 4.7E-16 -

Te-129m 3.9E-04 6.3E-14 1.3E-15 -

Te-129 2.5E-04 3.9E-14 7.9E-16 -

Te-131m 1.4E-05 6.0E-14 1.2E-15 -

Te-131 3.2E-06 1.4E-14 2.7E-16 -

Te-132 5.7E-04 9.5E-13 1.9E-14 -

Te-133m 1.1E-24 1.6E-31 3.1E-33 -

Te-134 1.8E-30 3.3E-37 6.5E-39 -

Ba-137m 2.1E+00 2.3E-11 4.7E-13 -

Ba-139 4.2E-20 3.9E-27 7.8E-29 -

Ba-140 4.0E-05 1.7E-14 3.4E-16 -

La-140 4.4E-05 1.3E-14 2.6E-16 -

La-141 2.0E-12 6.6E-20 1.3E-21 -

La-142 7.7E-20 6.5E-27 1.3E-28 -

Ce-141 1.7E-05 2.8E-15 5.6E-17 -

Ce-143 1.8E-07 7.0E-16 1.4E-17 -

Ce-144 1.1E-04 2.5E-15 5.0E-17 -

Pr-143 6.4E-06 2.5E-15 4.9E-17 -

Pr-144 1.1E-04 2.5E-15 4.9E-17 -

Np-239 1.0E-05 2.4E-14 4.8E-16 -

Na-24 3.9E-05 3.7E-13 7.4E-15 4.3E-06 Cr-51 1.2E+00 2.5E-10 5.0E-12 1.3E-01 Mn-54 5.7E+00 1.4E-10 2.7E-12 4.4E-01 Fe-55 6.8E+00 1.0E-10 2.0E-12 4.3E-01 cale US460 SDAA 12.2-24 Revision 1

PCWS PCWS Particulate Reactor Pool Water PCWS Surge Tank Radionuclide Demineralizers Filter (Ci) (Ci/g) (Ci/g) (Ci)

Fe-59 1.8E-01 2.5E-11 4.9E-13 2.1E-02 Co-58 4.5E+01 3.8E-09 7.7E-11 5.0E+00 Co-60 3.4E+00 4.5E-11 9.0E-13 2.0E-01 Ni-63 1.9E+00 2.3E-11 4.5E-13 1.1E-01 Zn-65 1.5E+00 4.3E-11 8.6E-13 1.3E-01 Zr-95 3.5E-01 3.2E-11 6.5E-13 3.8E-02 Ag-110m 4.0E+00 1.1E-10 2.2E-12 3.3E-01 W-187 8.0E-03 4.8E-11 9.6E-13 9.0E-04 H-3 - 1.2E-07 1.2E-07 -

C-14 - 1.0E-12 1.0E-12 -

N-16 - - - -

Ar-41 - - - -

cale US460 SDAA 12.2-25 Revision 1

Strengths PCWS PCWS Reactor Pool PCWS Surge Energy (MeV) Particulate rgy Group Demineralizers Water Tank Filter Lower Bound Upper Bound (/s) (/s) (/s) (/s) 1 1.00E-02 2.00E-02 4.2E+09 6.0E+09 1.6E-02 3.6E+08 2 2.00E-02 3.00E-02 6.3E+09 2.1E+10 2.2E-02 3.3E+08 3 3.00E-02 4.50E-02 9.3E+09 1.3E+10 3.2E-02 1.5E+08 4 4.50E-02 6.00E-02 1.3E+09 2.7E+09 5.1E-03 1.2E+08 5 6.00E-02 7.00E-02 7.2E+08 5.7E+09 1.8E-02 6.2E+07 6 7.00E-02 7.50E-02 3.0E+08 3.4E+09 5.8E-03 2.8E+07 7 7.50E-02 1.00E-01 2.9E+09 1.4E+10 2.2E-02 9.3E+07 8 1.00E-01 1.50E-01 1.3E+09 4.8E+09 8.7E-03 1.2E+08 9 1.50E-01 2.00E-01 1.2E+09 3.3E+09 3.1E-02 8.9E+07 10 2.00E-01 2.60E-01 6.2E+08 9.7E+08 2.0E-03 5.2E+07 11 2.60E-01 3.00E-01 4.5E+09 3.4E+10 4.8E-02 2.1E+07 12 3.00E-01 4.00E-01 6.2E+10 4.7E+11 4.7E-01 5.0E+08 13 4.00E-01 4.50E-01 5.8E+09 2.5E+09 3.7E-03 4.8E+08 14 4.50E-01 5.10E-01 2.2E+09 8.1E+09 2.6E-02 2.2E+07 15 5.10E-01 5.12E-01 5.0E+11 5.0E+11 8.5E-01 5.5E+10 16 5.12E-01 6.00E-01 3.0E+10 4.6E+10 2.5E-01 1.0E+07 17 6.00E-01 7.00E-01 3.6E+11 1.3E+11 9.7E-01 1.4E+10 18 7.00E-01 8.00E-01 2.1E+11 6.7E+10 9.3E-01 6.7E+09 19 8.00E-01 9.00E-01 1.9E+12 1.7E+12 3.1E+00 2.0E+11 20 9.00E-01 1.00E+00 5.0E+10 1.7E+10 2.8E-02 4.1E+09 21 1.00E+00 1.20E+00 1.7E+11 4.0E+10 2.0E-01 1.1E+10 22 1.20E+00 1.33E+00 6.9E+10 1.8E+10 6.1E-02 4.3E+09 23 1.33E+00 1.44E+00 1.0E+11 2.2E+10 6.3E-02 6.7E+09 24 1.44E+00 1.50E+00 6.2E+09 2.0E+09 3.4E-03 5.1E+08 25 1.50E+00 1.57E+00 2.2E+10 7.0E+09 1.2E-02 1.8E+09 26 1.57E+00 1.66E+00 3.8E+07 1.9E+07 3.1E-05 3.0E+06 27 1.66E+00 1.80E+00 8.4E+09 8.4E+09 1.4E-02 9.3E+08 28 1.80E+00 2.00E+00 2.6E+07 1.7E+07 2.2E-05 2.1E+06 29 2.00E+00 2.15E+00 1.7E+06 4.4E+06 4.3E-06 1.2E+05 30 2.15E+00 2.35E+00 1.5E+06 2.1E+06 2.2E-06 8.6E+04 31 2.35E+00 2.50E+00 8.6E+04 1.1E+06 9.6E-07 7.7E+01 32 2.50E+00 2.75E+00 8.2E+05 8.5E+07 1.4E-04 8.4E+04 33 2.75E+00 3.00E+00 6.8E+05 7.7E+07 1.3E-04 7.7E+04 34 3.00E+00 3.50E+00 5.3E+02 1.6E+03 2.7E-09 1.5E-04 35 3.50E+00 4.00E+00 1.1E+03 1.2E+05 2.1E-07 1.2E+02 36 4.00E+00 4.50E+00 1.2E+01 1.4E+03 2.3E-09 1.3E+00 37 4.50E+00 5.00E+00 - - - -

38 5.00E+00 5.50E+00 - - - -

39 5.50E+00 6.00E+00 - - - -

40 6.00E+00 6.50E+00 - - - -

41 6.50E+00 7.00E+00 - - - -

42 7.00E+00 7.50E+00 - - - -

43 7.50E+00 8.00E+00 - - - -

cale US460 SDAA 12.2-26 Revision 1

PCWS PCWS Reactor Pool PCWS Surge Energy (MeV) Particulate rgy Group Demineralizers Water Tank Filter Lower Bound Upper Bound (/s) (/s) (/s) (/s) 44 8.00E+00 1.00E+01 - - - -

45 1.00E+01 1.20E+01 - - - -

46 1.20E+01 1.40E+01 - - - -

47 1.40E+01 2.00E+01 - - - -

Total 3.6E+12 3.2E+12 7.2E+00 3.1E+11 cale US460 SDAA 12.2-27 Revision 1

Assumptions Model Parameter Value S degasifier -

ontents CVCS Letdown eometry Vertical Cylinder Source dimensions Diameter=138 in, Height=193 in Shield thickness of steel shell 1.75 in Volume 12500 Gallons and HCW collection tanks -

puts Table 11.2-3 eometry Vertical Cylinder Source dimensions Diameter=12 ft, Height=21 ft Shield thickness of steel shell 0.25 in Volume 14400 gallons S oil separator -

puts Table 11.2-3 eometry Horizontal Cylinder Source dimensions Diameter=51 in, Height=118 in Shield thickness of steel shell 0.25 in and HCW granulated activated charcoal (GAC) units -

econtamination Factors -

Cr-51 256 Mn-54 107 Co-58 13.2 Co-60 6.7 Ag-110m 3250 Antimony 7.1 Nb-95 639 eometry Vertical Cylinder Source dimensions of vessel Diameter=71 in, Height=71 in Shield thickness of steel shell 0.25 in reverse osmosis (RO) unit -

econtamination factors -

All nuclides 10 eometry Horizontal Cylinder Source dimensions Diameter=59 in, Length=102 in Shield thickness of steel shell 0.25 in and HCW sample tanks -

eometry Vertical Cylinder Source dimensions Diameter=12 ft, Height=21 ft Shield thickness of steel shell 0.25 in m dryer and holdup tank -

puts RO Rejects eometry Vertical Cylinder Source dimensions Diameter=65.0 in, Height=118 in Shield thickness of steel shell 0.25 in processing skid -

cale US460 SDAA 12.2-28 Revision 1

Model Parameter Value puts LCW Filters, Ixs, Accumulators, and Polishers total Accumulation (LCW Processing Skid) eometry Horizontal Cylinder Source Dimensions Diameter=71 in, Length=299 in Shield thickness of steel shell 0.25 in Additional Shielding 1 in Steel

Assumes the plant consists of 6 NPMs operating on an 18-month refueling cycle.

cale US460 SDAA 12.2-29 Revision 1

Radionuclide Content LCW Collection Tank HCW Collection Tank LCW Sample Tank HCW Sample Tank Isotope (Ci/Tank) (Ci/Tank) (Ci/Tank) (Ci/Tank)

Kr83m - - - -

Kr85m - - - -

Kr85 - - - -

Kr87 - - - -

Kr88 - - - -

Kr89 - - - -

Xe131m - - - -

Xe133m - - - -

Xe133 - - - -

Xe135m - - - -

Xe135 - - - -

Xe137 - - - -

Xe138 - - - -

Br82 3.9E-05 3.6E-05 1.9E-13 9.4E-11 Br83 2.3E-04 2.1E-04 - -

Br84 1.1E-04 9.6E-05 - -

Br85 1.3E-05 1.2E-05 - -

I129 6.5E-10 6.0E-10 6.5E-14 6.0E-14 I130 3.2E-04 3.0E-04 1.6E-20 8.8E-13 I131 8.2E-03 1.3E-02 1.3E-07 6.7E-07 I132 3.8E-03 3.5E-03 2.1E-09 1.5E-08 I133 1.2E-02 1.2E-02 6.0E-14 2.4E-09 I134 2.2E-03 2.0E-03 - -

I135 7.9E-03 7.2E-03 - 2.2E-15 Rb86m 3.1E-07 2.3E-08 - -

Rb86 1.8E-03 1.3E-04 4.8E-07 5.9E-08 Rb88 3.0E-01 2.2E-02 - -

Rb89 1.4E-02 1.0E-03 - -

Cs132 3.6E-05 2.6E-06 2.2E-09 6.8E-10 Cs134 2.6E-01 1.9E-02 1.5E-04 1.1E-05 Cs135m 2.1E-04 1.6E-05 - -

Cs136 5.6E-02 4.2E-03 1.1E-05 1.6E-06 Cs137 1.3E-01 9.8E-03 7.7E-05 5.8E-06 Cs138 1.1E-01 8.4E-03 - -

P32 3.6E-10 1.5E-10 1.3E-14 1.0E-14 Co57 2.7E-12 1.1E-12 2.6E-16 1.1E-16 Sr89 1.6E-05 6.6E-06 2.5E-09 7.1E-10 Sr90 2.6E-06 1.0E-06 2.6E-10 1.0E-10 Sr91 8.6E-06 3.4E-06 - 5.3E-16 Sr92 4.6E-06 1.8E-06 - -

Y90 6.3E-07 2.5E-07 2.6E-10 9.3E-11 Y91m 4.6E-06 1.8E-06 - 3.4E-16 Y91 2.4E-06 9.6E-07 1.9E-10 8.9E-11 Y92 3.9E-06 1.6E-06 - -

Y93 1.8E-06 7.3E-07 - 2.3E-16 cale US460 SDAA 12.2-30 Revision 1

LCW Collection Tank HCW Collection Tank LCW Sample Tank HCW Sample Tank Isotope (Ci/Tank) (Ci/Tank) (Ci/Tank) (Ci/Tank)

Zr97 2.7E-06 1.1E-06 2.2E-19 5.0E-14 Nb95 4.9E-06 2.8E-05 5.3E-09 1.1E-08 Mo99 4.9E-03 2.0E-03 2.4E-09 2.8E-08 Mo101 1.9E-04 7.4E-05 - -

Tc99m 4.5E-03 1.8E-03 2.3E-09 2.7E-08 Tc99 9.2E-08 3.7E-08 9.3E-12 3.7E-12 Ru103 4.7E-06 1.9E-06 3.2E-10 1.6E-10 Ru105 1.5E-06 6.2E-07 - -

Ru106 2.9E-06 1.2E-06 2.8E-10 1.2E-10 Rh103m 4.6E-06 1.9E-06 3.2E-10 1.6E-10 Rh105 3.2E-06 1.3E-06 1.7E-14 3.5E-12 Rh106 2.9E-06 1.2E-06 2.8E-10 1.2E-10 Ag110 9.1E-06 3.1E-05 7.1E-10 3.0E-09 Sb124 7.0E-09 2.8E-09 5.5E-13 2.6E-13 Sb125 5.2E-08 2.1E-08 5.1E-12 2.1E-12 Sb127 2.6E-07 1.1E-07 5.9E-13 2.6E-12 Sb129 3.3E-07 1.3E-07 - -

Te125m 7.6E-06 3.0E-06 5.9E-10 2.8E-10 Te127m 2.9E-05 1.2E-05 2.5E-09 1.1E-09 Te127 1.1E-04 4.5E-05 2.5E-09 1.1E-09 Te129m 8.2E-05 3.3E-05 5.3E-09 2.8E-09 Te129 1.2E-04 4.7E-05 3.4E-09 1.8E-09 Te131m 2.7E-04 1.1E-04 2.3E-13 1.5E-10 Te131 1.3E-04 5.3E-05 5.1E-14 3.3E-11 Te132 2.0E-03 7.9E-04 2.1E-09 1.5E-08 Te133m 1.7E-04 6.7E-05 - -

Te134 2.4E-04 9.5E-05 - -

Ba137m 9.0E-03 3.7E-03 7.3E-05 5.4E-06 Ba139 4.5E-06 1.8E-06 - -

Ba140 2.4E-05 9.7E-06 7.7E-10 6.3E-10 La140 7.0E-06 2.8E-06 8.8E-10 7.0E-10 La141 1.4E-06 5.5E-07 - -

La142 6.6E-07 2.6E-07 - -

Ce141 3.7E-06 1.5E-06 2.4E-10 1.3E-10 Ce143 2.8E-06 1.1E-06 7.0E-15 2.3E-12 Ce144 3.1E-06 1.3E-06 3.0E-10 1.2E-10 Pr143 3.3E-06 1.3E-06 1.2E-10 9.7E-11 Pr144 3.1E-06 1.2E-06 3.0E-10 1.2E-10 Np239 5.9E-05 2.4E-05 1.2E-11 2.4E-10 Na24 2.4E-02 9.4E-03 1.6E-16 1.7E-10 Cr51 1.3E-03 5.1E-03 7.9E-08 4.2E-07 Mn54 6.8E-04 2.8E-03 6.5E-08 2.7E-07 Fe55 5.1E-04 2.1E-03 5.1E-08 2.1E-07 Fe59 1.3E-04 5.1E-04 9.3E-09 4.5E-08 Co58 2.0E-03 7.1E-02 1.6E-07 6.6E-06 cale US460 SDAA 12.2-31 Revision 1

LCW Collection Tank HCW Collection Tank LCW Sample Tank HCW Sample Tank Isotope (Ci/Tank) (Ci/Tank) (Ci/Tank) (Ci/Tank)

Co60 2.3E-04 9.2E-04 2.2E-08 9.2E-08 Ni63 1.1E-04 4.6E-04 1.1E-08 4.6E-08 Zn65 2.2E-04 8.8E-04 2.1E-08 8.6E-08 Zr95 1.7E-04 6.6E-04 1.3E-08 6.1E-08 Ag110m 5.6E-04 2.2E-03 5.2E-08 2.2E-07 W187 1.2E-03 1.4E-03 4.6E-14 6.0E-10 H3 1.2E+02 1.2E+01 1.2E+02 1.2E+01 C14 1.2E-02 7.7E-04 1.2E-02 7.7E-04 N16 - - - -

Ar41 - - - -

Total 1.2E+02 1.2E+01 1.2E+02 1.2E+01 cale US460 SDAA 12.2-32 Revision 1

Radionuclide Content LCW Reverse LCW Solids HCW Granulated Drum Dryer Isotope Osmosis Unit Collection Filter Activated Charcoal (Ci) (Ci) (Ci) (Ci/Drum)

Kr83m - - - -

Kr85m - - - -

Kr85 - - - -

Kr87 - - - -

Kr88 - - - -

Kr89 - - - -

Xe131m - - - -

Xe133m - - - -

Xe133 - - - -

Xe135m - - - -

Xe135 - - - -

Xe137 - - - -

Xe138 - - - -

Br82 1.5E-07 - - 1.5E-07 Br83 5.9E-08 - - 5.9E-08 Br84 6.1E-09 - - 6.1E-09 Br85 6.7E-11 - - 6.7E-11 I129 2.3E-11 - 1.2E-11 4.3E-10 I130 4.3E-07 - - 4.3E-07 I131 2.2E-04 - 2.5E-05 2.7E-04 I132 5.1E-06 - 5.9E-04 5.2E-06 I133 2.9E-05 - 5.0E-07 2.9E-05 I134 2.2E-07 - 6.5E-07 2.2E-07 I135 5.6E-06 - - 5.6E-06 Rb86m 1.1E-12 - - 1.1E-12 Rb86 8.4E-05 - 3.8E-12 1.6E-04 Rb88 1.8E-05 - - 1.8E-05 Rb89 7.1E-07 - - 7.1E-07 Cs132 9.8E-07 - - 1.1E-06 Cs134 1.7E-02 - - 2.7E-01 Cs135m 3.8E-08 - - 3.8E-08 Cs136 2.3E-03 - - 3.6E-03 Cs137 8.6E-03 - - 1.6E-01 Cs138 1.3E-05 - - 1.3E-05 P32 4.8E-12 - - 7.9E-12 Co57 5.5E-14 - - 6.9E-13 Sr89 4.3E-07 - 2.6E-06 1.8E-06 Sr90 5.3E-08 - - 9.8E-07 Sr91 5.2E-09 - - 5.2E-09 Sr92 7.7E-10 - - 7.7E-10 Y90 2.1E-08 - 1.8E-04 4.3E-07 Y91m 1.6E-09 - 1.9E-07 1.6E-09 Y91 4.4E-08 - 1.5E-07 2.1E-07 Y92 1.2E-09 - 4.8E-08 1.2E-09 cale US460 SDAA 12.2-33 Revision 1

LCW Reverse LCW Solids HCW Granulated Drum Dryer Isotope Osmosis Unit Collection Filter Activated Charcoal (Ci) (Ci) (Ci) (Ci/Drum)

Y93 1.2E-09 - - 1.2E-09 Zr97 2.9E-09 - - 2.9E-09 Nb95 9.5E-07 - 1.0E-02 9.0E-06 Mo99 2.0E-05 - - 2.0E-05 Mo101 2.9E-09 - - 2.9E-09 Tc99m 9.5E-06 - 1.1E-03 9.6E-06 Tc99 1.9E-09 - 2.6E-09 3.6E-08 Ru103 8.1E-08 - - 2.8E-07 Ru105 4.3E-10 - - 4.3E-10 Ru106 5.9E-08 - - 8.2E-07 Rh103m 3.5E-08 - 1.7E-05 1.2E-07 Rh105 7.3E-09 - 2.7E-08 7.3E-09 Rh106 2.6E-08 - 9.0E-05 3.6E-07 Ag110 6.6E-08 - 1.7E-03 8.0E-07 Sb124 1.3E-10 - 3.4E-08 6.3E-10 Sb125 1.1E-09 - 2.3E-06 1.8E-08 Sb127 1.5E-09 - 8.2E-08 1.5E-09 Sb129 9.0E-11 - 4.8E-09 9.0E-11 Te125m 1.4E-07 - 5.8E-07 6.5E-07 Te127m 5.5E-07 - 1.7E-08 4.3E-06 Te127 3.0E-07 - 2.9E-04 1.9E-06 Te129m 1.4E-06 - 1.3E-09 4.2E-06 Te129 3.9E-07 - 1.7E-04 1.2E-06 Te131m 5.1E-07 - - 5.1E-07 Te131 5.3E-08 - 7.0E-06 5.3E-08 Te132 9.4E-06 - - 9.6E-06 Te133m 9.8E-09 - - 9.8E-09 Te134 1.1E-08 - - 1.1E-08 Ba137m 6.6E-03 - 1.6E+00 1.2E-01 Ba139 3.9E-10 - - 3.9E-10 Ba140 3.0E-07 - - 4.7E-07 La140 1.4E-07 - 2.9E-05 2.2E-07 La141 3.4E-10 - - 3.4E-10 La142 6.3E-11 - - 6.3E-11 Ce141 6.2E-08 - 2.1E-08 1.8E-07 Ce143 5.8E-09 - - 5.8E-09 Ce144 6.3E-08 - - 8.0E-07 Pr143 4.4E-08 - 3.6E-07 7.0E-08 Pr144 2.7E-08 - 7.8E-05 3.5E-07 Np239 2.1E-07 - - 2.1E-07 Na24 2.2E-05 2.5E-03 - 2.2E-05 Cr51 1.3E-04 3.6E-02 3.3E-02 3.3E-04 Mn54 8.3E-05 1.8E-01 1.8E-01 1.1E-03 Fe55 6.4E-05 2.1E-01 - 1.1E-03 cale US460 SDAA 12.2-34 Revision 1

LCW Reverse LCW Solids HCW Granulated Drum Dryer Isotope Osmosis Unit Collection Filter Activated Charcoal (Ci) (Ci) (Ci) (Ci/Drum)

Fe59 1.3E-05 5.7E-03 - 5.1E-05 Co58 1.9E-03 1.2E+00 1.1E+00 1.1E-02 Co60 2.8E-05 1.0E-01 1.2E-01 5.0E-04 Ni63 1.4E-05 5.9E-02 - 2.7E-04 Zn65 2.6E-05 4.8E-02 - 3.2E-04 Zr95 1.8E-05 1.1E-02 - 9.5E-05 Ag110m 6.7E-05 1.2E-01 1.3E-01 8.2E-04 W187 3.7E-06 4.1E-04 - 3.7E-06 H3 - - - -

C14 - - - -

N16 - - - -

Ar41 - - - -

Total 3.7E-02 2.0E+00 3.2E+00 5.7E-01 cale US460 SDAA 12.2-35 Revision 1

Radionuclide Content LCW Processing Skid Oil Separator Isotope (Ci) (Ci)

Kr83m - -

Kr85m - -

Kr85 - -

Kr87 - -

Kr88 - -

Kr89 - -

Xe131m - -

Xe133m - -

Xe133 - -

Xe135m - -

Xe135 - -

Xe137 - -

Xe138 - -

Br82 1.7E-05 4.1E-06 Br83 6.6E-06 2.3E-05 Br84 6.8E-07 1.1E-05 Br85 7.4E-09 1.3E-06 I129 9.6E-08 6.7E-11 I130 4.8E-05 3.3E-05 I131 3.0E-02 8.4E-04 I132 5.7E-04 3.9E-04 I133 3.2E-03 1.3E-03 I134 2.4E-05 2.3E-04 I135 6.3E-04 8.1E-04 Rb86m 2.0E-11 9.6E-10 Rb86 3.1E-03 5.6E-06 Rb88 3.5E-04 9.6E-04 Rb89 1.4E-05 4.4E-05 Cs132 2.1E-05 1.1E-07 Cs134 8.7E+00 8.0E-04 Cs135m 7.2E-07 6.7E-07 Cs136 6.8E-02 1.7E-04 Cs137 6.0E+00 4.1E-04 Cs138 2.4E-04 3.6E-04 P32 8.7E-10 1.6E-11 Co57 1.1E-10 1.2E-13 Sr89 1.5E-04 7.1E-07 Sr90 2.1E-04 1.1E-07 Sr91 5.8E-07 3.7E-07 Sr92 8.6E-08 2.0E-07 Y90 9.4E-05 2.7E-08 Y91m 1.8E-07 2.0E-07 Y91 2.4E-05 1.0E-07 Y92 1.3E-07 1.7E-07 Y93 1.3E-07 7.9E-08 cale US460 SDAA 12.2-36 Revision 1

LCW Processing Skid Oil Separator Isotope (Ci) (Ci)

Zr97 3.2E-07 1.2E-07 Nb95 1.0E-03 2.1E-07 Mo99 2.3E-03 2.1E-04 Mo101 3.2E-07 8.1E-06 Tc99m 1.1E-03 2.0E-04 Tc99 7.9E-06 4.0E-09 Ru103 3.1E-05 2.0E-07 Ru105 4.8E-08 6.7E-08 Ru106 1.4E-04 1.3E-07 Rh103m 1.4E-05 2.0E-07 Rh105 8.1E-07 1.4E-07 Rh106 6.1E-05 1.3E-07 Ag110 1.2E-04 3.9E-07 Sb124 7.1E-08 3.0E-10 Sb125 3.5E-06 2.3E-09 Sb127 1.7E-07 1.1E-08 Sb129 1.0E-08 1.4E-08 Te125m 7.4E-05 3.3E-07 Te127m 5.2E-04 1.2E-06 Te127 2.3E-04 4.9E-06 Te129m 4.7E-04 3.6E-0 Te129 1.3E-04 5.1E-06 Te131m 5.7E-05 1.2E-05 Te131 5.9E-06 5.8E-06 Te132 1.1E-03 8.5E-05 Te133m 1.1E-0 7.3E-06 Te134 1.2E-06 1.0E-05 Ba137m 4.6E+00 3.9E-04 Ba139 4.3E-08 1.9E-07 Ba140 5.2E-05 1.0E-06 La140 2.5E-05 3.0E-07 La141 3.8E-08 6.0E-08 La142 7.0E-09 2.8E-08 Ce141 2.0E-05 1.6E-07 Ce143 6.5E-07 1.2E-07 Ce144 1.3E-04 1.4E-07 Pr143 7.8E-06 1.4E-07 Pr144 5.5E-05 1.3E-07 Np239 2.3E-05 2.5E-06 Na24 2.5E-03 1.0E-03 Cr51 3.6E-02 5.8E-05 Mn54 1.8E-01 3.0E-05 Fe55 2.1E-01 2.2E-05 Fe59 5.7E-03 5.6E-06 Co58 1.2E+00 8.5E-05 cale US460 SDAA 12.2-37 Revision 1

LCW Processing Skid Oil Separator Isotope (Ci) (Ci)

Co60 1.0E-01 9.8E-06 Ni63 5.9E-02 4.9E-06 Zn65 4.8E-02 9.4E-06 Zr95 1.1E-02 7.2E-06 Ag110m 1.2E-01 2.4E-05 W187 4.1E-04 5.2E-05 H3 - 6.1E-01 C14 - 2.0E-05 N16 - -

Ar41 - -

Total 2.1E+01 6.2E-01 cale US460 SDAA 12.2-38 Revision 1

Strengths LCW HCW LCW Sample HCW Sample Lower Bound Upper Bound Collection Collection rgy Group Tank Tank Tank Tank (MeV) (MeV) (/s) (/s) (/s) (/s) 1 1.00E-02 2.00E-02 6.8E+08 7.5E+07 3.8E+06 3.7E+05 2 2.00E-02 3.00E-02 4.5E+08 8.2E+07 1.2E+05 9.1E+03 3 3.00E-02 4.50E-02 6.0E+08 7.3E+07 3.1E+05 2.5E+04 4 4.50E-02 6.00E-02 2.5E+08 2.9E+07 3.4E+04 2.5E+03 5 6.00E-02 7.00E-02 2.3E+08 3.0E+07 3.1E+04 3.8E+03 6 7.00E-02 7.50E-02 5.7E+07 1.2E+07 4.2E+03 3.2E+02 7 7.50E-02 1.00E-01 3.2E+08 4.0E+07 3.0E+04 4.5E+03 8 1.00E-01 1.50E-01 5.0E+08 1.1E+08 5.4E+03 1.7E+03 9 1.50E-01 2.00E-01 5.6E+08 5.3E+07 6.5E+04 9.9E+03 10 2.00E-01 2.60E-01 2.5E+08 4.9E+07 2.7E+03 7.7E+02 11 2.60E-01 3.00E-01 3.2E+08 6.8E+07 4.4E+04 8.1E+03 12 3.00E-01 4.00E-01 1.3E+09 5.2E+08 1.7E+05 4.8E+04 13 4.00E-01 4.50E-01 2.9E+08 5.4E+07 1.4E+02 3.5E+02 14 4.50E-01 5.10E-01 1.5E+09 1.4E+08 8.5E+04 6.9E+03 15 5.10E-01 5.12E-01 3.2E+07 8.0E+08 1.8E+03 7.3E+04 16 5.12E-01 6.00E-01 3.2E+09 6.5E+08 1.3E+06 1.0E+05 17 6.00E-01 7.00E-01 9.3E+09 1.1E+09 7.4E+06 5.7E+05 18 7.00E-01 8.00E-01 9.3E+09 9.1E+08 5.2E+06 4.0E+05 19 8.00E-01 9.00E-01 3.6E+09 3.1E+09 5.8E+05 3.2E+05 20 9.00E-01 1.00E+00 9.2E+08 1.3E+08 6.8E+02 2.9E+03 21 1.00E+00 1.20E+00 3.4E+09 4.4E+08 4.2E+05 5.8E+04 22 1.20E+00 1.33E+00 8.0E+08 1.8E+08 7.9E+04 1.4E+04 23 1.33E+00 1.44E+00 4.7E+09 6.8E+08 1.6E+05 1.6E+04 24 1.44E+00 1.50E+00 8.5E+07 3.6E+07 8.3E+01 3.5E+02 25 1.50E+00 1.57E+00 4.7E+07 2.2E+07 7.4E+02 1.3E+03 26 1.57E+00 1.66E+00 1.7E+07 5.2E+06 3.1E+01 2.7E+01 27 1.66E+00 1.80E+00 1.3E+08 7.8E+07 3.1E+01 1.2E+03 28 1.80E+00 2.00E+00 2.5E+09 1.9E+08 1.9E+00 1.2E+01 29 2.00E+00 2.15E+00 1.0E+08 1.1E+07 6.6E-01 4.7E+00 30 2.15E+00 2.35E+00 7.2E+08 5.5E+07 5.1E-01 2.3E+00 31 2.35E+00 2.50E+00 1.8E+07 4.5E+06 3.1E-01 1.3E+00 32 2.50E+00 2.75E+00 1.1E+09 2.3E+08 1.2E+00 4.5E+00 33 2.75E+00 3.00E+00 4.4E+08 1.7E+08 2.3E-02 3.1E+00 34 3.00E+00 3.50E+00 7.7E+07 5.9E+06 9.2E-03 7.2E-03 35 3.50E+00 4.00E+00 1.5E+07 1.6E+06 8.0E-08 4.9E-03 36 4.00E+00 4.50E+00 2.9E+06 2.3E+05 4.9E-11 5.3E-05 37 4.50E+00 5.00E+00 2.1E+07 1.6E+06 - -

38 5.00E+00 5.50E+00 4.0E+04 3.0E+03 - -

39 5.50E+00 6.00E+00 - - - -

40 6.00E+00 6.50E+00 - - - -

41 6.50E+00 7.00E+00 - - - -

42 7.00E+00 7.50E+00 - - - -

43 7.50E+00 8.00E+00 - - - -

cale US460 SDAA 12.2-39 Revision 1

LCW HCW LCW Sample HCW Sample Lower Bound Upper Bound Collection Collection rgy Group Tank Tank Tank Tank (MeV) (MeV) (/s) (/s) (/s) (/s) 44 8.00E+00 1.00E+01 - - - -

45 1.00E+01 1.20E+01 - - - -

46 1.20E+01 1.40E+01 - - - -

47 1.40E+01 2.00E+01 - - - -

Total 4.8E+10 1.0E+10 2.0E+07 2.0E+06 cale US460 SDAA 12.2-40 Revision 1

Strengths Lower Bound Upper Bound LCW RO LCW SCF HCW GAC Drum Dryer rgy Group (MeV) (MeV) (/s) (/s) (/s) (/s) 1 1.00E-02 2.00E-02 3.0E+06 9.2E+07 8.9E+07 4.4E+07 2 2.00E-02 3.00E-02 2.1E+06 1.0E+08 9.9E+07 2.4E+07 3 3.00E-02 4.50E-02 2.7E+07 3.9E+07 3.8E+09 3.9E+08 4 4.50E-02 6.00E-02 8.4E+05 3.0E+07 2.7E+07 1.2E+07 5 6.00E-02 7.00E-02 4.5E+06 1.7E+07 1.3E+07 1.2E+07 6 7.00E-02 7.50E-02 1.7E+05 8.1E+06 5.5E+06 2.2E+06 7 7.50E-02 1.00E-01 5.1E+06 2.3E+07 2.2E+07 1.5E+07 8 1.00E-01 1.50E-01 1.1E+06 3.2E+07 6.8E+07 7.7E+06 9 1.50E-01 2.00E-01 1.4E+07 2.3E+07 1.5E+07 2.5E+07 10 2.00E-01 2.60E-01 6.8E+05 1.5E+07 1.5E+07 4.8E+06 11 2.60E-01 3.00E-01 9.7E+06 5.7E+06 6.0E+06 1.6E+07 12 3.00E-01 4.00E-01 4.3E+07 1.4E+08 1.3E+08 6.7E+07 13 4.00E-01 4.50E-01 1.6E+05 1.8E+08 1.8E+08 1.3E+06 14 4.50E-01 5.10E-01 1.0E+07 7.6E+06 6.0E+06 1.5E+08 15 5.10E-01 5.12E-01 2.1E+07 1.3E+10 1.2E+10 1.2E+08 16 5.12E-01 6.00E-01 1.5E+08 3.5E+06 6.4E+06 2.4E+09 17 6.00E-01 7.00E-01 7.9E+08 5.3E+09 6.0E+10 1.3E+10 18 7.00E-01 8.00E-01 5.9E+08 2.4E+09 2.4E+09 9.5E+09 19 8.00E-01 9.00E-01 1.7E+08 5.3E+10 4.9E+10 9.6E+08 20 9.00E-01 1.00E+00 9.4E+05 1.6E+09 1.6E+09 1.0E+07 21 1.00E+00 1.20E+00 7.5E+07 5.1E+09 4.6E+09 4.0E+08 22 1.20E+00 1.33E+00 1.7E+07 2.1E+09 2.3E+09 3.7E+07 23 1.33E+00 1.44E+00 2.1E+07 3.1E+09 3.2E+09 3.1E+08 24 1.44E+00 1.50E+00 1.3E+05 1.9E+08 2.0E+08 1.3E+06 25 1.50E+00 1.57E+00 4.7E+05 6.7E+08 6.8E+08 4.6E+06 26 1.57E+00 1.66E+00 7.5E+03 1.1E+06 2.2E+06 1.7E+04 27 1.66E+00 1.80E+00 4.0E+05 2.2E+08 2.0E+08 2.0E+06 28 1.80E+00 2.00E+00 1.6E+05 7.8E+05 1.2E+06 1.6E+05 29 2.00E+00 2.15E+00 1.0E+04 4.6E+04 2.3E+05 1.0E+04 30 2.15E+00 2.35E+00 7.8E+04 4.4E+04 1.5E+05 7.8E+04 31 2.35E+00 2.50E+00 3.7E+03 4.0E+01 5.2E+04 3.7E+03 32 2.50E+00 2.75E+00 4.9E+05 4.8E+07 4.8E+04 4.9E+05 33 2.75E+00 3.00E+00 4.0E+05 4.4E+07 9.3E+02 4.0E+05 34 3.00E+00 3.50E+00 5.7E+03 8.4E-02 3.6E+02 5.7E+03 35 3.50E+00 4.00E+00 1.6E+03 7.0E+04 2.4E-02 1.6E+03 36 4.00E+00 4.50E+00 2.2E+02 7.7E+02 - 2.2E+02 37 4.50E+00 5.00E+00 1.3E+03 - - 1.3E+03 38 5.00E+00 5.50E+00 2.4E+00 - - 2.4E+00 39 5.50E+00 6.00E+00 - - - -

40 6.00E+00 6.50E+00 - - - -

41 6.50E+00 7.00E+00 - - - -

42 7.00E+00 7.50E+00 - - - -

43 7.50E+00 8.00E+00 - - - -

44 8.00E+00 1.00E+01 - - - -

45 1.00E+01 1.20E+01 - - - -

cale US460 SDAA 12.2-41 Revision 1

Lower Bound Upper Bound LCW RO LCW SCF HCW GAC Drum Dryer rgy Group (MeV) (MeV) (/s) (/s) (/s) (/s) 46 1.20E+01 1.40E+01 - - - -

47 1.40E+01 2.00E+01 - - - -

Total 2.0E+09 8.7E+10 1.4E+11 2.8E+10 cale US460 SDAA 12.2-42 Revision 1

Strengths LCW Processing Lower Bound Upper Bound Oil Separator Energy Group Skid (MeV) (MeV) (/s) (/s) 1 1.00E-02 2.00E-02 1.6E+09 4.4E+06 2 2.00E-02 3.00E-02 9.5E+08 6.0E+06 3 3.00E-02 4.50E-02 1.4E+10 4.6E+06 4 4.50E-02 6.00E-02 4.3E+08 1.7E+06 5 6.00E-02 7.00E-02 3.2E+08 1.3E+06 6 7.00E-02 7.50E-02 8.2E+07 5.2E+05 7 7.50E-02 1.00E-01 4.4E+08 2.2E+06 8 1.00E-01 1.50E-01 3.2E+08 1.0E+07 9 1.50E-01 2.00E-01 5.4E+08 2.9E+06 10 2.00E-01 2.60E-01 1.9E+08 4.5E+06 11 2.60E-01 3.00E-01 3.7E+08 4.6E+06 12 3.00E-01 4.00E-01 2.2E+09 3.1E+07 13 4.00E-01 4.50E-01 1.9E+08 4.4E+06 14 4.50E-01 5.10E-01 4.8E+09 6.7E+06 15 5.10E-01 5.12E-01 1.3E+10 1.9E+06 16 5.12E-01 6.00E-01 7.8E+10 5.6E+07 17 6.00E-01 7.00E-01 4.5E+11 6.7E+07 18 7.00E-01 8.00E-01 3.1E+11 4.7E+07 19 8.00E-01 9.00E-01 6.8E+10 3.6E+07 20 9.00E-01 1.00E+00 1.6E+09 7.8E+06 21 1.00E+00 1.20E+00 1.6E+10 2.6E+07 22 1.20E+00 1.33E+00 2.6E+09 1.4E+07 23 1.33E+00 1.44E+00 1.3E+10 5.2E+07 24 1.44E+00 1.50E+00 1.9E+08 3.4E+06 25 1.50E+00 1.57E+00 6.7E+08 1.1E+06 26 1.57E+00 1.66E+00 2.1E+06 5.3E+05 27 1.66E+00 1.80E+00 2.3E+08 6.9E+06 28 1.80E+00 2.00E+00 4.4E+06 9.0E+06 29 2.00E+00 2.15E+00 5.8E+05 7.7E+05 30 2.15E+00 2.35E+00 1.7E+06 2.5E+06 31 2.35E+00 2.50E+00 3.1E+05 4.3E+05 32 2.50E+00 2.75E+00 4.9E+07 2.2E+07 33 2.75E+00 3.00E+00 4.4E+07 1.8E+07 34 3.00E+00 3.50E+00 1.1E+05 2.7E+05 35 3.50E+00 4.00E+00 9.0E+04 1.0E+05 36 4.00E+00 4.50E+00 4.8E+03 1.1E+04 37 4.50E+00 5.00E+00 2.4E+04 6.7E+04 38 5.00E+00 5.50E+00 4.6E+01 1.3E+02 39 5.50E+00 6.00E+00 - -

40 6.00E+00 6.50E+00 - -

41 6.50E+00 7.00E+00 - -

42 7.00E+00 7.50E+00 - -

43 7.50E+00 8.00E+00 - -

44 8.00E+00 1.00E+01 - -

cale US460 SDAA 12.2-43 Revision 1

LCW Processing Lower Bound Upper Bound Oil Separator Energy Group Skid (MeV) (MeV) (/s) (/s) 45 1.00E+01 1.20E+01 - -

46 1.20E+01 1.40E+01 - -

47 1.40E+01 2.00E+01 - -

Total 9.8E+11 4.6E+08 cale US460 SDAA 12.2-44 Revision 1

Model Parameter Value WS guard bed -

ontents Guard Bed Buildup eometry Vertical Cylinder Source dimensions of vessel Diameter=2 ft, Height=3.2 ft Shield thickness of steel shell 0.25 in WS decay bed (four each per train; two trains) -

puts Sum of Decay Bed 5a, 6a, 7a, and 8a eometry Vertical Cylinder Source dimensions of vessel Diameter=6.5 ft, Height=4.4 ft Shield thickness o fsteel shell 0.25 in cale US460 SDAA 12.2-45 Revision 1

Radionuclide Content Charcoal Decay Charcoal Decay Charcoal Decay Charcoal Decay Isotope Guard Bed (Ci)

Bed 5A (Ci) Bed 6A (Ci) Bed 7A (Ci) Bed 8A (Ci)

Kr83m 4.6E-04 5.6E-04 1.4E-06 6.4E-08 6.3E-09 Kr85m 3.0E-03 5.3E-03 3.6E-04 2.4E-05 1.7E-06 Kr85 7.6E-01 2.8E+00 2.8E+00 2.8E+00 2.8E+00 Kr87 8.2E-04 8.8E-04 6.7E-08 5.1E-12 3.9E-16 Kr88 3.9E-03 5.7E-03 8.1E-05 1.2E-06 1.7E-08 Kr89 2.4E-06 2.4E-06 - - -

Xe131m 3.7E-01 9.8E-01 3.6E-01 1.3E-01 4.7E-02 Xe133m 1.9E-01 2.4E-01 1.0E-03 5.2E-06 1.1E-07 Xe133 2.0E+01 3.9E+01 4.1E+00 4.2E-01 4.3E-02 Xe135m 1.2E-04 1.2E-04 9.8E-06 9.8E-07 9.8E-08 Xe135 8.3E-02 8.3E-02 1.8E-04 1.6E-05 1.6E-06 Xe137 9.7E-06 9.7E-06 - - -

Xe138 1.2E-04 1.2E-04 - - -

Br82 1.5E-06 1.5E-06 1.5E-07 1.5E-08 1.5E-09 Br83 5.7E-07 5.7E-07 5.7E-08 5.7E-09 5.7E-10 Br84 5.8E-08 5.8E-08 5.8E-09 5.8E-10 5.8E-11 Br85 6.4E-10 6.4E-10 6.4E-11 6.4E-12 6.4E-13 I129 2.5E-07 2.5E-07 2.5E-08 2.5E-09 2.5E-10 I130 4.2E-06 4.2E-06 4.2E-07 4.2E-08 4.2E-09 I131 1.6E-03 1.6E-03 1.6E-04 1.6E-05 1.6E-06 I132 9.1E-06 9.1E-06 9.1E-07 9.1E-08 9.1E-09 I133 2.7E-04 2.7E-04 2.7E-05 2.7E-06 2.7E-07 I134 2.0E-06 2.0E-06 2.0E-07 2.0E-08 2.0E-09 I135 5.4E-05 5.4E-05 5.4E-06 5.4E-07 5.4E-08 Rb86m - - - - -

Rb86 - - - - -

Rb88 3.9E-03 5.7E-03 8.1E-05 1.2E-06 1.7E-08 Rb89 2.4E-06 2.4E-06 - - -

Cs132 - - - - -

Cs134 - - - - -

Cs135m - - - - -

Cs136 - - - - -

Cs137 7.2E-06 7.2E-06 - - -

Cs138 1.2E-04 1.2E-04 - - -

P32 - - - - -

Co57 - - - - -

Sr89 2.4E-06 2.4E-06 - - -

Sr90 - - - - -

Sr91 - - - - -

Sr92 - - - - -

Y90 - - - - -

Y91m - - - - -

Y91 - - - - -

Y92 - - - - -

Y93 - - - - -

cale US460 SDAA 12.2-46 Revision 1

Charcoal Decay Charcoal Decay Charcoal Decay Charcoal Decay Isotope Guard Bed (Ci)

Bed 5A (Ci) Bed 6A (Ci) Bed 7A (Ci) Bed 8A (Ci)

Zr97 - - - - -

Nb95 - - - - -

Mo99 - - - - -

Mo101 - - - - -

Tc99m - - - - -

Tc99 - - - - -

Ru103 - - - - -

Ru105 - - - - -

Ru106 - - - - -

Rh103m - - - - -

Rh105 - - - - -

Rh106 - - - - -

Ag110 - - - - -

Sb124 - - - - -

Sb125 - - - - -

Sb127 - - - - -

Sb129 - - - - -

Te125m - - - - -

Te127m - - - - -

Te127 - - - - -

Te129m - - - - -

Te129 - - - - -

Te131m - - - - -

Te131 - - - - -

Te132 - - - - -

Te133m - - - - -

Te134 - - - - -

Ba137m 6.8E-06 6.8E-06 - - -

Ba139 - - - - -

Ba140 - - - - -

La140 - - - - -

La141 - - - - -

La142 - - - - -

Ce141 - - - - -

Ce143 - - - - -

Ce144 - - - - -

Pr143 - - - - -

Pr144 - - - - -

Np239 - - - - -

Na24 - - - - -

Cr51 - - - - -

Mn54 - - - - -

Fe55 - - - - -

Fe59 - - - - -

Co58 - - - - -

cale US460 SDAA 12.2-47 Revision 1

Charcoal Decay Charcoal Decay Charcoal Decay Charcoal Decay Isotope Guard Bed (Ci)

Bed 5A (Ci) Bed 6A (Ci) Bed 7A (Ci) Bed 8A (Ci)

Co60 - - - - -

Ni63 - - - - -

Zn65 - - - - -

Zr95 - - - - -

Ag110m - - - - -

W187 - - - - -

H3 - - - - -

C14 - - - - -

N16 - - - - -

Ar41 1.4E-02 3.8E-02 1.4E-02 5.2E-03 1.9E-03 Total 2.1E+01 4.3E+01 7.3E+00 3.4E+00 2.9E+00 cale US460 SDAA 12.2-48 Revision 1

Isotope Activity (Ci)

Kr83m 8.8E-02 Kr85m 3.7E-01 Kr85 6.8E+01 Kr87 2.0E-01 Kr88 5.9E-01 Kr89 1.0E-02 Xe131m 1.6E+00 Xe133m 1.3E+00 Xe133 9.9E+01 Xe135m 1.2E-01 Xe135 2.7E+00 Xe137 3.6E-02 Xe138 1.4E-01 Br82 2.5E-05 Br83 1.4E-04 Br84 6.4E-05 Br85 5.9E-06 I129 4.0E-10 I130 2.0E-04 I131 5.1E-03 I132 2.4E-03 I133 7.7E-03 I134 1.4E-03 I135 4.9E-03 Rb86m 1.3E-07 Rb86 1.7E-03 Rb88 3.1E-01 Rb89 1.3E-02 Cs132 3.4E-05 Cs134 2.5E-01 Cs135m 2.0E-04 Cs136 5.4E-02 Cs137 1.3E-01 Cs138 1.1E-01 P32 1.9E-10 Co57 1.5E-12 Sr89 8.9E-06 Sr90 1.4E-06 Sr91 4.6E-06 Sr92 2.4E-06 Y90 3.3E-07 Y91m 2.4E-06 Y91 1.3E-06 Y92 2.1E-06 Y93 9.8E-07 Zr97 1.5E-06 Nb95 2.6E-06 cale US460 SDAA 12.2-49 Revision 1

Isotope Activity (Ci)

Mo99 2.6E-03 Mo101 9.4E-05 Tc99m 2.4E-03 Tc99 4.9E-08 Ru103 2.5E-06 Ru105 8.2E-07 Ru106 1.6E-06 Rh103m 2.5E-06 Rh105 1.7E-06 Rh106 1.6E-06 Ag110 4.1E-06 Sb124 3.7E-09 Sb125 2.8E-08 Sb127 1.4E-07 Sb129 1.7E-07 Te125m 4.0E-06 Te127m 1.5E-05 Te127 6.1E-05 Te129m 4.4E-05 Te129 6.2E-05 Te131m 1.4E-04 Te131 7.0E-05 Te132 1.0E-03 Te133m 8.9E-05 Te134 1.3E-04 Ba137m 3.7E-02 Ba139 2.4E-06 Ba140 1.3E-05 La140 3.7E-06 La141 7.3E-07 La142 3.5E-07 Ce141 2.0E-06 Ce143 1.5E-06 Ce144 1.7E-06 Pr143 1.7E-06 Pr144 1.7E-06 Np239 3.1E-05 Na24 1.3E-02 Cr51 7.1E-04 Mn54 3.6E-04 Fe55 2.7E-04 Fe59 6.9E-05 Co58 1.1E-03 Co60 1.2E-04 Ni63 6.0E-05 Zn65 1.2E-04 Zr95 8.9E-05 cale US460 SDAA 12.2-50 Revision 1

Isotope Activity (Ci)

Ag110m 3.0E-04 W187 6.4E-04 H3 1.2E+02 C14 1.2E-02 N16 3.5E-02 Ar41 9.6E+00

The radiological content of the liquid in the degasifier is primary coolant that has been processed through the S demineralizers using the shared systems fuel failure fraction, and decayed for 10 N-16 half-lives (71.3 nds). The CVCS demineralizer decontamination factors are provided in Table 11.1-2.

cale US460 SDAA 12.2-51 Revision 1

Scale Final Safety Analysis Report Source Terms - Source Strengths Charcoal Decay Charcoal Decay Charcoal Decay Charcoal Decay Energy (MeV) Guard Bed nergy Group Bed 5A Bed 6A Bed 7A Bed 8A Lower Bound Upper Bound photons/sec photons/sec photons/sec photons/sec photons/sec 1 1.00E-02 2.00E-02 1.3E+09 2.7E+09 7.0E+08 4.8E+08 4.6E+08 2 2.00E-02 3.00E-02 8.1E+09 1.8E+10 5.1E+09 2.0E+09 8.7E+08 3 3.00E-02 4.50E-02 3.1E+11 6.0E+11 6.6E+10 7.7E+09 1.2E+09 4 4.50E-02 6.00E-02 2.8E+08 6.0E+08 1.8E+08 1.4E+08 1.3E+08 5 6.00E-02 7.00E-02 1.2E+08 2.6E+08 8.1E+07 6.2E+07 6.0E+07 6 7.00E-02 7.50E-02 4.8E+07 1.0E+08 3.4E+07 2.6E+07 2.5E+07 7 7.50E-02 1.00E-01 2.6E+11 5.1E+11 5.4E+10 5.7E+09 6.6E+08 8 1.00E-01 1.50E-01 1.6E+08 3.4E+08 1.1E+08 8.7E+07 8.5E+07 9 1.50E-01 2.00E-01 8.2E+08 1.8E+09 3.9E+08 1.4E+08 7.9E+07 10 2.00E-01 2.60E-01 3.7E+09 4.0E+09 3.3E+07 2.2E+07 2.1E+07 11 2.60E-01 3.00E-01 2.9E+07 5.5E+07 1.4E+07 9.6E+06 9.1E+06 12 3.00E-01 4.00E-01 1.2E+08 1.8E+08 2.7E+07 1.4E+07 1.3E+07 13 4.00E-01 4.50E-01 2.8E+07 3.1E+07 2.0E+06 1.9E+06 1.9E+06 14 4.50E-01 5.10E-01 4.1E+06 5.8E+06 1.1E+06 1.0E+06 9.9E+05 15 5.10E-01 5.12E-01 6.2E+07 2.3E+08 2.3E+08 2.3E+08 2.3E+08 16 5.12E-01 6.00E-01 7.0E+07 2.2E+08 2.1E+08 2.1E+08 2.1E+08 17 6.00E-01 7.00E-01 9.2E+07 9.3E+07 8.6E+05 1.9E+05 1.2E+05 18 7.00E-01 8.00E-01 5.2E+06 6.0E+06 2.3E+05 2.5E+04 4.6E+03 19 8.00E-01 9.00E-01 3.7E+07 5.2E+07 7.6E+05 2.2E+04 2.2E+03 20 9.00E-01 1.00E+00 1.3E+07 1.9E+07 2.9E+05 6.6E+03 6.7E+02 21 1.00E+00 1.20E+00 8.8E+06 1.1E+07 2.1E+05 1.1E+04 1.2E+03 22 1.20E+00 1.33E+00 5.4E+08 1.4E+09 5.3E+08 2.0E+08 7.3E+07 23 1.33E+00 1.44E+00 8.2E+06 1.0E+07 9.2E+04 1.9E+03 1.1E+02 24 1.44E+00 1.50E+00 4.7E+05 5.6E+05 2.4E+04 2.0E+03 2.1E+02 25 1.50E+00 1.57E+00 1.9E+07 2.8E+07 4.0E+05 6.1E+03 1.4E+02 Radiation Sources 26 1.57E+00 1.66E+00 1.0E+06 1.4E+06 1.9E+04 3.6E+02 2.5E+01 27 1.66E+00 1.80E+00 3.8E+06 5.1E+06 3.4E+05 1.0E+05 3.6E+04 28 1.80E+00 2.00E+00 3.3E+07 4.7E+07 6.7E+05 9.9E+03 1.8E+02 29 2.00E+00 2.15E+00 1.4E+07 2.0E+07 2.6E+05 4.0E+03 7.8E+01 30 2.15E+00 2.35E+00 2.5E+07 3.6E+07 5.1E+05 7.4E+03 1.2E+02

Scale Final Safety Analysis Report Charcoal Decay Charcoal Decay Charcoal Decay Charcoal Decay Energy (MeV) Guard Bed nergy Group Bed 5A Bed 6A Bed 7A Bed 8A Lower Bound Upper Bound photons/sec photons/sec photons/sec photons/sec photons/sec 31 2.35E+00 2.50E+00 5.1E+07 7.3E+07 1.0E+06 1.5E+04 2.4E+02 32 2.50E+00 2.75E+00 8.8E+06 1.1E+07 9.3E+04 1.3E+03 1.9E+01 33 2.75E+00 3.00E+00 5.8E+05 7.9E+05 9.4E+03 1.3E+02 2.0E+00 34 3.00E+00 3.50E+00 8.5E+05 1.2E+06 1.4E+04 2.0E+02 2.9E+00 35 3.50E+00 4.00E+00 1.3E+05 1.8E+05 2.4E+03 3.6E+01 6.5E-01 36 4.00E+00 4.50E+00 2.4E+04 3.4E+04 4.7E+02 6.8E+00 1.0E-01 37 4.50E+00 5.00E+00 2.8E+05 4.0E+05 5.7E+03 8.2E+01 1.2E+00 38 5.00E+00 5.50E+00 5.2E+02 7.5E+02 1.1E+01 1.5E-01 2.2E-03 39 5.50E+00 6.00E+00 - - - - -

40 6.00E+00 6.50E+00 - - - - -

41 6.50E+00 7.00E+00 - - - - -

42 7.00E+00 7.50E+00 - - - - -

43 7.50E+00 8.00E+00 - - - - -

44 8.00E+00 1.00E+01 - - - - -

45 1.00E+01 1.20E+01 - - - - -

46 1.20E+01 1.40E+01 - - - - -

47 1.40E+01 2.00E+01 - - - - -

Total 5.8E+11 1.1E+12 1.3E+11 1.7E+10 4.1E+09 Radiation Sources

Model Parameter Value nt resin storage tank- -

ontents Spent Resin from the CVCS and PCWS eometry Vertical Cylinder Source dimensions of vessel Diameter=12 ft, height=14 ft Shield thickness of steel shell 0.25 in se separator tank- -

puts Spent Resin from the LRWS eometry Vertical Cylinder Source dimensions of vessel Diameter=12 ft, height=17 ft Shield thickness of steel shell 0.25 in integrity container (HIC)- -

puts Spent Resins from SRST eometry Vertical Cylinder Source dimensions of container diameter=62 in, height=75 in Array of HICs 2x1 and 3x1 cale US460 SDAA 12.2-54 Revision 1

Content Spent Resin Storage Tank Phase Separator Tank HIC from SRST Isotope (Ci) (Ci) (Ci/HIC)

Kr83m 2.4E-11 - -

Kr85m 7.7E-12 -

Kr85 9.1E-09 - 2.9E-09 Kr87 - - -

Kr88 - - -

Kr89 - - -

Xe131m 4.4E-02 - 6.8E-20 Xe133m 1.6E-03 - -

Xe133 1.4E-01 - -

Xe135m 1.8E-06 - -

Xe135 1.5E-04 - -

Xe137 - - -

Xe138 - - -

Br82 9.1E-05 1.7E-05 -

Br83 6.1E-12 6.6E-06 -

Br84 - 6.8E-07 -

Br85 - 7.4E-09 -

I129 4.5E-04 9.6E-08 1.6E-04 I130 1.6E-05 4.8E-05 -

I131 1.7E+00 3.0E-02 -

I132 1.6E-02 5.7E-04 -

I133 9.5E-03 3.2E-03 -

I134 6.4E-09 2.4E-05 -

I135 1.1E-05 6.3E-04 -

Rb86m 3.9E-15 2.0E-11 -

Rb86 4.1E-02 3.1E-03 9.0E-14 Rb88 1.2E-06 3.5E-04 -

Rb89 3.9E-08 1.4E-05 -

Cs132 9.1E-05 2.1E-05 -

Cs134 2.0E+03 8.7E+00 3.7E+02 Cs135m 7.3E-09 7.2E-07 -

Cs136 6.2E-01 6.8E-02 2.9E-17 Cs137 1.8E+03 6.0E+00 6.0E+02 Cs138 1.6E-06 2.4E-04 -

P32 7.8E-08 8.7E-10 -

Co57 1.7E-07 1.1E-10 1.0E-08 Sr89 4.8E-02 1.5E-04 1.2E-06 Sr90 7.2E-01 2.1E-04 2.4E-01 Sr91 7.2E-08 5.8E-07 -

Sr92 7.9E-10 8.6E-08 -

Y90 7.2E-01 9.4E-05 2.4E-01 Y91m 4.6E-08 1.8E-07 -

Y91 9.4E-03 2.4E-05 9.0E-07 Y92 3.1E-09 1.3E-07 -

Y93 2.0E-08 1.3E-07 -

cale US460 SDAA 12.2-55 Revision 1

Spent Resin Storage Tank Phase Separator Tank HIC from SRST Isotope (Ci) (Ci) (Ci/HIC)

Zr97 2.3E-07 3.2E-07 -

Nb95 1.6E+00 1.0E-03 4.8E-04 Mo99 2.6E-02 2.3E-03 -

Mo101 2.7E-10 3.2E-07 -

Tc99m 2.5E-02 1.1E-03 -

Tc99 2.7E-02 7.9E-06 9.7E-03 Ru103 8.1E-03 3.1E-05 1.4E-08 Ru105 7.8E-10 4.8E-08 -

Ru106 2.6E-01 1.4E-04 2.5E-02 Rh103m 8.0E-03 1.4E-05 1.4E-08 Rh105 3.5E-06 8.1E-07 -

Rh106 2.6E-01 6.1E-05 2.5E-02 Ag110 4.6E-01 1.2E-04 2.4E-02 Sb124 2.9E-05 7.1E-08 3.4E-09 Sb125 9.5E-03 3.5E-06 2.1E-03 Sb127 3.2E-06 1.7E-07 -

Sb129 1.6E-10 1.0E-08 -

Te125m 3.0E-02 7.4E-05 5.2E-04 Te127m 3.8E-01 5.2E-04 1.6E-03 Te127 3.7E-01 2.3E-04 1.6E-03 Te129m 1.0E-01 4.7E-04 2.2E-08 Te129 6.5E-02 1.3E-04 1.4E-08 Te131m 1.7E-04 5.7E-05 -

Te131 3.8E-05 5.9E-06 -

Te132 1.5E-02 1.1E-03 -

Te133m 3.5E-09 1.1E-06 -

Te134 2.8E-09 1.2E-06 -

Ba137m 1.7E+03 4.6E+00 5.7E+02 Ba139 2.1E-10 4.3E-08 -

Ba140 4.1E-03 5.2E-05 6.0E-20 La140 4.7E-03 2.5E-05 6.9E-20 La141 5.2E-10 3.8E-08 -

La142 3.7E-11 7.0E-09 -

Ce141 4.4E-03 2.0E-05 5.8E-10 Ce143 2.3E-06 6.5E-07 -

Ce144 2.0E-01 1.3E-04 1.3E-02 Pr143 6.9E-04 7.8E-06 9.9E-20 Pr144 2.0E-01 5.5E-05 1.3E-02 Np239 2.1E-04 2.3E-05 -

Na24 1.3E-03 2.5E-03 -

Cr51 2.3E+00 3.6E-02 2.3E-08 Mn54 5.5E+01 1.8E-01 4.2E+00 Fe55 1.0E+02 2.1E-01 2.2E+01 Fe59 4.7E-01 5.7E-03 3.4E-06 Co58 5.7E+01 1.2E+00 2.3E-02 cale US460 SDAA 12.2-56 Revision 1

Spent Resin Storage Tank Phase Separator Tank HIC from SRST Isotope (Ci) (Ci) (Ci/HIC)

Co60 5.5E+01 1.0E-01 1.5E+01 Ni63 3.5E+01 5.9E-02 1.2E+01 Zn65 1.3E+01 4.8E-02 6.4E-01 Zr95 1.1E+00 1.1E-02 2.2E-04 Ag110m 3.4E+01 1.2E-01 1.8E+00 W187 8.3E-03 4.1E-04 -

H3 - - -

C14 - - -

N16 - - -

Ar41 - - -

Total 5.8E+03 2.1E+01 1.6E+03 cale US460 SDAA 12.2-57 Revision 1

Strengths Spent Resin Phase Separator High Integrity Energy (MeV) ergy Group Storage Tank Tank Container Lower Bound Upper Bound photons/sec photons/sec photons/sec 1 1.00E-02 2.00E-02 3.9E+11 1.6E+09 1.0E+11 2 2.00E-02 3.00E-02 2.3E+11 9.5E+08 5.3E+10 3 3.00E-02 4.50E-02 4.6E+12 1.4E+10 1.5E+12 4 4.50E-02 6.00E-02 1.0E+11 4.3E+08 2.7E+10 5 6.00E-02 7.00E-02 4.8E+10 3.2E+08 1.2E+10 6 7.00E-02 7.50E-02 1.9E+10 8.2E+07 5.0E+09 7 7.50E-02 1.00E-01 7.4E+10 4.5E+08 1.8E+10 8 1.00E-01 1.50E-01 6.4E+10 3.2E+08 1.5E+10 9 1.50E-01 2.00E-01 3.5E+10 5.4E+08 7.6E+09 10 2.00E-01 2.60E-01 3.6E+10 1.9E+08 7.2E+09 11 2.60E-01 3.00E-01 1.3E+10 3.7E+08 1.5E+09 12 3.00E-01 4.00E-01 9.0E+10 2.2E+09 4.0E+09 13 4.00E-01 4.50E-01 4.9E+10 1.9E+08 2.8E+09 14 4.50E-01 5.10E-01 1.1E+12 4.8E+09 2.0E+11 15 5.10E-01 5.12E-01 6.4E+11 1.3E+10 1.1E+09 16 5.12E-01 6.00E-01 1.8E+13 7.8E+10 3.3E+12 17 6.00E-01 7.00E-01 1.3E+14 4.5E+11 3.2E+13 18 7.00E-01 8.00E-01 7.1E+13 3.1E+11 1.3E+13 19 8.00E-01 9.00E-01 8.1E+12 6.8E+10 7.7E+11 20 9.00E-01 1.00E+00 4.3E+11 1.6E+09 2.2E+10 21 1.00E+00 1.20E+00 4.5E+12 1.6E+10 1.0E+12 22 1.20E+00 1.33E+00 1.1E+12 2.6E+09 3.0E+11 23 1.33E+00 1.44E+00 3.5E+12 1.3E+10 7.0E+11 24 1.44E+00 1.50E+00 5.3E+10 1.9E+08 2.7E+09 25 1.50E+00 1.57E+00 1.8E+11 6.7E+08 9.5E+09 26 1.57E+00 1.66E+00 4.7E+08 2.1E+06 1.6E+07 27 1.66E+00 1.80E+00 1.1E+10 2.3E+08 1.6E+07 28 1.80E+00 2.00E+00 2.3E+08 4.4E+06 1.2E+07 29 2.00E+00 2.15E+00 2.2E+07 5.8E+05 1.1E+06 30 2.15E+00 2.35E+00 7.8E+07 1.7E+06 1.0E+07 31 2.35E+00 2.50E+00 7.8E+06 3.1E+05 5.6E+05 32 2.50E+00 2.75E+00 3.3E+07 4.9E+07 1.2E+05 33 2.75E+00 3.00E+00 2.4E+07 4.4E+07 4.6E+04 34 3.00E+00 3.50E+00 2.2E+05 1.1E+05 1.6E+04 35 3.50E+00 4.00E+00 3.7E+04 9.0E+04 6.8E+00 36 4.00E+00 4.50E+00 4.3E+02 4.8E+03 -

37 4.50E+00 5.00E+00 8.3E+01 2.4E+04 -

38 5.00E+00 5.50E+00 1.6E-01 4.6E+01 -

39 5.50E+00 6.00E+00 - - -

40 6.00E+00 6.50E+00 - - -

41 6.50E+00 7.00E+00 - - -

42 7.00E+00 7.50E+00 - - -

43 7.50E+00 8.00E+00 - - -

44 8.00E+00 1.00E+01 - - -

cale US460 SDAA 12.2-58 Revision 1

Spent Resin Phase Separator High Integrity Energy (MeV) ergy Group Storage Tank Tank Container Lower Bound Upper Bound photons/sec photons/sec photons/sec 45 1.00E+01 1.20E+01 - - -

46 1.20E+01 1.40E+01 - - -

47 1.40E+01 2.00E+01 - - -

Total 2.4E+14 9.8E+11 5.3E+13 cale US460 SDAA 12.2-59 Revision 1

Full Fuel Storage Single Spent Fuel Rack Energy (MeV) Assembly (48 hour5.555556e-4 days <br />0.0133 hours <br />7.936508e-5 weeks <br />1.8264e-5 months <br /> decay time Energy Group (48 hr decay time) for all 660 Assemblies)

Lower Bound Upper Bound photons/sec photons/sec 1 1.00E-02 2.00E-02 7.8E+16 5.1E+19 2 2.00E-02 3.00E-02 2.2E+16 1.4E+19 3 3.00E-02 4.50E-02 2.4E+16 1.6E+19 4 4.50E-02 6.00E-02 1.0E+16 6.9E+18 5 6.00E-02 7.00E-02 4.2E+15 2.8E+18 6 7.00E-02 7.50E-02 1.1E+15 7.0E+17 7 7.50E-02 1.00E-01 1.9E+16 1.3E+19 8 1.00E-01 1.50E-01 8.1E+16 5.4E+19 9 1.50E-01 2.00E-01 4.3E+15 2.8E+18 10 2.00E-01 2.60E-01 2.6E+16 1.7E+19 11 2.60E-01 3.00E-01 2.0E+16 1.3E+19 12 3.00E-01 4.00E-01 1.5E+16 1.0E+19 13 4.00E-01 4.50E-01 1.8E+15 1.2E+18 14 4.50E-01 5.10E-01 1.9E+16 1.3E+19 15 5.10E-01 5.12E-01 1.8E+15 1.2E+18 16 5.12E-01 6.00E-01 8.6E+15 5.7E+18 17 6.00E-01 7.00E-01 1.9E+16 1.2E+19 18 7.00E-01 8.00E-01 3.5E+16 2.3E+19 19 8.00E-01 9.00E-01 5.9E+15 3.9E+18 20 9.00E-01 1.00E+00 3.9E+15 2.6E+18 21 1.00E+00 1.20E+00 3.6E+15 2.4E+18 22 1.20E+00 1.33E+00 1.6E+15 1.0E+18 23 1.33E+00 1.44E+00 9.0E+14 5.9E+17 24 1.44E+00 1.50E+00 4.0E+14 2.6E+17 25 1.50E+00 1.57E+00 4.6E+13 3.0E+16 26 1.57E+00 1.66E+00 1.1E+16 7.2E+18 27 1.66E+00 1.80E+00 1.1E+14 7.5E+16 28 1.80E+00 2.00E+00 5.4E+14 3.5E+17 29 2.00E+00 2.15E+00 4.1E+14 2.7E+17 30 2.15E+00 2.35E+00 4.9E+14 3.2E+17 31 2.35E+00 2.50E+00 7.3E+13 4.8E+16 32 2.50E+00 2.75E+00 4.0E+14 2.6E+17 33 2.75E+00 3.00E+00 9.1E+12 6.0E+15 34 3.00E+00 3.50E+00 3.4E+12 2.2E+15 35 3.50E+00 4.00E+00 3.9E+08 2.6E+11 36 4.00E+00 4.50E+00 5.5E+07 3.6E+10 37 4.50E+00 5.00E+00 9.1E+07 6.0E+10 38 5.00E+00 5.50E+00 1.5E+07 1.0E+10 39 5.50E+00 6.00E+00 8.8E+06 5.8E+09 40 6.00E+00 6.50E+00 5.1E+06 3.3E+09 41 6.50E+00 7.00E+00 2.9E+06 1.9E+09 42 7.00E+00 7.50E+00 1.7E+06 1.1E+09 43 7.50E+00 8.00E+00 9.9E+05 6.5E+08 cale US460 SDAA 12.2-60 Revision 1

Full Fuel Storage Single Spent Fuel Rack Energy (MeV) Assembly (48 hour5.555556e-4 days <br />0.0133 hours <br />7.936508e-5 weeks <br />1.8264e-5 months <br /> decay time Energy Group (48 hr decay time) for all 660 Assemblies)

Lower Bound Upper Bound photons/sec photons/sec 44 8.00E+00 1.00E+01 1.2E+06 7.7E+08 45 1.00E+01 1.20E+01 6.0E+04 4.0E+07 46 1.20E+01 1.40E+01 - -

47 1.40E+01 2.00E+01 - -

Total 4.2E+17 2.8E+20 cale US460 SDAA 12.2-61 Revision 1

Full Fuel Storage Single Spent Fuel Rack Energy (MeV) Assembly (48 hour5.555556e-4 days <br />0.0133 hours <br />7.936508e-5 weeks <br />1.8264e-5 months <br /> decay time Energy Group (48 hr decay time) for all 660 Assemblies)

Lower Bound Upper Bound neutrons/sec neutrons/sec 1 1.0E-11 1.0E-08 1.2E-04 8.0E-02 2 1.0E-08 3.0E-08 1.4E-04 9.1E-02 3 3.0E-08 5.0E-08 1.0E-02 6.7E+00 4 5.0E-08 1.0E-07 7.8E-03 5.2E+00 5 1.0E-07 2.3E-07 6.6E-02 4.4E+01 6 2.3E-07 3.3E-07 6.0E-02 3.9E+01 7 3.3E-07 4.1E-07 4.4E-02 2.9E+01 8 4.1E-07 8.0E-07 3.6E-01 2.3E+02 9 8.0E-07 1.0E-06 1.8E-01 1.2E+02 10 1.0E-06 1.1E-06 1.8E-01 1.2E+02 11 1.1E-06 1.3E-06 2.2E-01 1.4E+02 12 1.3E-06 1.9E-06 7.8E-01 5.2E+02 13 1.9E-06 3.1E-06 2.1E+00 1.4E+03 14 3.1E-06 1.1E-05 2.2E+01 1.5E+04 15 1.1E-05 2.9E-05 9.1E+01 6.0E+04 16 2.9E-05 1.0E-04 6.5E+02 4.3E+05 17 1.0E-04 5.8E-04 9.8E+03 6.4E+06 18 5.8E-04 3.0E-03 1.1E+05 7.6E+07 19 3.0E-03 1.5E-02 1.2E+06 8.2E+08 20 1.5E-02 1.1E-01 2.5E+07 1.7E+10 21 1.1E-01 4.1E-01 1.5E+08 9.6E+10 22 4.1E-01 9.1E-01 3.2E+08 2.1E+11 23 9.1E-01 1.4E+00 3.2E+08 2.1E+11 24 1.4E+00 1.8E+00 2.3E+08 1.5E+11 25 1.8E+00 3.0E+00 4.8E+08 3.1E+11 26 3.0E+00 6.4E+00 4.2E+08 2.7E+11 27 6.4E+00 2.0E+01 4.3E+07 2.8E+10 Total 2.0E+09 1.3E+12 cale US460 SDAA 12.2-62 Revision 1

Component (quantity) Material ter (4) Rh-103 al wire (4) 316LSS lation(1) Al2O3 r sheath (1) 316LSS r sheath (6) 316LSS rmocouple-type K chromel-alumel (2) Chromel Alumel Parameter Value ber of irradiation cycles 1-40 tron flux 3.1E+14n/cm2-sec cale US460 SDAA 12.2-63 Revision 1

Cycle 1 Cycle 40 Energy Lower Bound Energy Upper Bound Energy Group Discharge 3-Day Decay (MeV) (MeV)

(photons/sec) (photons/sec) 1 2.00E-02 3.50E-02 2.5E+13 1.1E+11 2 3.50E-02 5.00E-02 1.2E+13 5.9E+10 3 5.00E-02 7.50E-02 1.4E+13 4.5E+10 4 7.50E-02 1.25E-01 1.4E+13 9.1E+10 5 1.25E-01 1.75E-01 6.2E+12 5.3E+11 6 1.75E-01 2.50E-01 4.7E+12 8.0E+10 7 2.50E-01 4.00E-01 8.2E+12 6.4E+11 8 4.00E-01 9.00E-01 5.6E+13 3.6E+12 9 9.00E-01 1.35E+00 3.6E+12 6.8E+12 10 1.35E+00 1.80E+00 8.0E+12 9.9E+09 11 1.80E+00 2.20E+00 9.8E+12 1.7E+08 12 2.20E+00 2.60E+00 3.8E+11 1.6E+06 13 2.60E+00 3.00E+00 3.6E+11 8.0E+08 14 3.00E+00 3.50E+00 6.2E+10 1.9E+06 15 3.50E+00 4.00E+00 4.3E+07 6.5E+05 16 4.00E+00 4.50E+00 7.2E+06 6.8E+03 17 4.50E+00 5.00E+00 5.5E+06 -

18 5.00E+00 1.00E+01 2.6E+09 -

Total 1.6E+14 1.2E+13 cale US460 SDAA 12.2-64 Revision 1

Parameter Value Neutron flux at control rod tip 5.9E+13n/cm2-sec CRA tip irradiation duration 1-40 cycles Control Rod Assembly component Material Absorber Ag-In-Cd Stack support X-750 Cladding 304 SS Lower end plug 308 SS cale US460 SDAA 12.2-65 Revision 1

Cycle 1 Energy Lower Energy Upper ergy Group 0-Day Decay 3-Day Decay 30-Day Decay Bound (MeV) Bound (MeV)

Photons/sec-kg 1 2.00E-02 3.50E-02 1.3E+15 1.0E+13 6.8E+12 2 3.50E-02 5.00E-02 7.3E+14 2.3E+12 1.2E+12 3 5.00E-02 7.50E-02 6.8E+14 2.1E+12 1.1E+12 4 7.50E-02 1.25E-01 8.1E+14 2.2E+12 1.2E+12 5 1.25E-01 1.75E-01 3.6E+14 9.1E+11 5.1E+11 6 1.75E-01 2.50E-01 2.8E+14 2.5E+12 1.4E+12 7 2.50E-01 4.00E-01 4.3E+14 4.6E+12 1.5E+12 8 4.00E-01 9.00E-01 1.4E+15 4.6E+14 4.3E+14 9 9.00E-01 1.35E+00 1.9E+15 4.9E+13 4.5E+13 10 1.35E+00 1.80E+00 2.2E+14 6.6E+13 6.2E+13 11 1.80E+00 2.20E+00 1.9E+14 2.9E+10 2.7E+10 12 2.20E+00 2.60E+00 1.2E+12 1.2E+08 1.2E+08 13 2.60E+00 3.00E+00 2.5E+11 5.6E+06 2.8E+06 14 3.00E+00 3.50E+00 3.9E+10 3.4E+05 2.5E+05 15 3.50E+00 4.00E+00 1.3E+06 6.4E+03 3.6E+03 16 4.00E+00 4.50E+00 7.4E+04 2.0E+01 2.0E-12 17 4.50E+00 5.00E+00 9.3E+01 0.0E+00 0.0E+00 18 5.00E+00 1.00E+01 6.3E+01 0.0E+00 0.0E+00 Total 8.2E+15 6.0E+14 5.5E+14 cale US460 SDAA 12.2-66 Revision 1

Cycle 1 Energy Lower Energy Upper ergy Group 0-Day Decay 3-Day Decay 30-Day Decay Bound (MeV) Bound (MeV)

Photons/sec-kg 1 2.00E-02 3.50E-02 2.8E+15 1.2E+15 3.9E+14 2 3.50E-02 5.00E-02 9.9E+14 5.5E+14 1.7E+14 3 5.00E-02 7.50E-02 1.5E+15 5.0E+14 1.5E+14 4 7.50E-02 1.25E-01 1.1E+15 5.5E+14 1.7E+14 5 1.25E-01 1.75E-01 4.5E+14 2.8E+14 1.2E+14 6 1.75E-01 2.50E-01 3.2E+14 1.7E+14 5.3E+13 7 2.50E-01 4.00E-01 4.6E+14 2.6E+14 9.2E+13 8 4.00E-01 9.00E-01 1.9E+16 1.3E+16 6.2E+15 9 9.00E-01 1.35E+00 7.7E+14 6.1E+14 3.8E+14 10 1.35E+00 1.80E+00 4.3E+15 4.1E+15 3.0E+15 11 1.80E+00 2.20E+00 6.3E+14 4.4E+14 3.2E+14 12 2.20E+00 2.60E+00 9.9E+12 3.0E+12 2.2E+12 13 2.60E+00 3.00E+00 6.5E+12 4.3E+11 3.1E+11 14 3.00E+00 3.50E+00 1.1E+12 4.7E+07 3.5E+07 15 3.50E+00 4.00E+00 1.1E+10 7.9E+05 5.0E+05 16 4.00E+00 4.50E+00 4.0E+09 1.7E+03 1.6E-10 17 4.50E+00 5.00E+00 3.9E+09 0.0E+00 0.0E+00 18 5.00E+00 1.00E+01 8.2E+09 0.0E+00 0.0E+00 Total 3.2E+16 2.1E+16 1.1E+16 cale US460 SDAA 12.2-67 Revision 1

Parameter Value Containment release delay 0 Containment release duration 1E-05 hr Containment leak rate 0.2 %/day Containment leak rate after 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> 0.1 %/day Aerosol fraction of non-noble gases released 100%

Bioshield envelope volume 1.3E+04 ft3 Primary coolant water density 44.5 lbm/ft3 Air density 0.07 lbm/ft3 Containment air volume 3.7E+03 ft3 Combined water volume 2.3E+03 ft3 cale US460 SDAA 12.2-68 Revision 1

Volume Medium Time Integrated Dose (Rad) actor and containment Water 1 hour1.157407e-5 days <br />2.777778e-4 hours <br />1.653439e-6 weeks <br />3.805e-7 months <br /> 6.7E+02 36 hours4.166667e-4 days <br />0.01 hours <br />5.952381e-5 weeks <br />1.3698e-5 months <br /> 6.0E+03 3 days 7.7E+03 30 days 1.4E+04 100 days 1.5E+04 Containment vessel Air 1 hour1.157407e-5 days <br />2.777778e-4 hours <br />1.653439e-6 weeks <br />3.805e-7 months <br /> 2.6E+05 36 hours4.166667e-4 days <br />0.01 hours <br />5.952381e-5 weeks <br />1.3698e-5 months <br /> 2.4E+06 3 days 3.2E+06 30 days 6.9E+06 100 days 1.0E+07 Bioshield envelope Air and water 1 hour1.157407e-5 days <br />2.777778e-4 hours <br />1.653439e-6 weeks <br />3.805e-7 months <br /> 3.2E+01 36 hours4.166667e-4 days <br />0.01 hours <br />5.952381e-5 weeks <br />1.3698e-5 months <br /> 7.8E+02 3 days 1.4E+03 30 days 1.3E+04 100 days 5.6E+04 cale US460 SDAA 12.2-69 Revision 1

Parameter Value ary coolant leak rate 160 lbm/day-NPM h fraction of primary coolant leaks 40%

release from primary coolant leaks 100%

ition coefficients for evaporation and leaks:

ble gases and tritium Table 11.3-4 logens rticulates dines (pool evaporation only) ary coolant source term Table 11.1-4 l water source term Table 12.2-9 l evaporation rate: 1300 lb/hr ol surface water temperature 100 degrees F ea of pool water surface 9300 ft2 velocity over water surface 30 ft/min om air temperature 73 degrees F om air relative humidity 68%

S pump valve room leak 3 lbm/day asifier room leak 8 lbm/day mal ventilation air change rates in RXB:

ol air space (100elevation) 1 air/change-hr CS pump/valve rooms (35-8elevation) 2 air/change-hr gasifier rooms (24 elevation) 2 air/change-hr l air space volume 2.66E+10 ml S pump valve room volume 1.20E+08 ml asifier room volume 2.55E+08 ml cale US460 SDAA 12.2-70 Revision 1

Air Space above Reactor CVCS Pump Room LWRS Degasifier Room Pool Airborne Radionuclide Airborne Concentration Airborne Concentration Concentration

(µCi/ml) (µCi/ml) (µCi/ml)

Kr83m 2.0E-09 2.0E-09 5.1E-15 Kr85m 9.3E-09 9.3E-09 -

Kr85 1.8E-06 1.8E-06 -

Kr87 4.3E-09 4.3E-09 -

Kr88 1.4E-08 1.4E-08 -

Kr89 4.8E-11 4.8E-11 -

Xe131m 4.2E-08 4.2E-08 1.2E-08 Xe133m 3.6E-08 3.6E-08 1.4E-08 Xe133 2.7E-06 2.7E-06 2.1E-07 Xe135m 1.5E-09 1.5E-09 1.9E-09 Xe135 6.9E-08 6.9E-08 1.0E-09 Xe137 1.8E-10 1.8E-10 -

Xe138 1.6E-09 1.6E-09 -

Br82 2.6E-13 2.6E-13 2.2E-16 Br83 1.3E-12 1.3E-12 3.7E-22 Br84 4.2E-13 4.2E-13 -

Br85 1.0E-14 1.0E-14 -

I129 4.3E-18 4.3E-18 1.1E-20 I130 2.1E-12 2.1E-12 2.3E-16 I131 5.4E-11 5.4E-11 1.1E-11 I132 2.2E-11 2.2E-11 2.7E-14 I133 8.2E-11 8.2E-11 9.6E-13 I134 1.1E-11 1.1E-11 -

I135 5.0E-11 5.0E-11 3.6E-16 Rb86m 1.5E-18 1.5E-18 -

Rb86 1.9E-13 1.9E-13 2.9E-14 Rb88 7.6E-09 7.6E-09 -

Rb89 2.8E-11 2.8E-11 -

Cs132 3.7E-15 3.7E-15 4.8E-16 Cs134 2.7E-11 2.7E-11 4.5E-12 Cs135m 1.6E-14 1.6E-14 -

Cs136 5.8E-12 5.8E-12 8.6E-13 Cs137 1.4E-11 1.4E-11 2.3E-12 Cs138 6.4E-10 6.4E-10 -

P32 5.2E-19 5.2E-19 2.4E-20 Co57 3.9E-21 3.9E-21 2.0E-22 Sr89 3.1E-14 3.1E-14 1.2E-15 Sr90 3.7E-15 3.7E-15 1.9E-16 Sr91 1.2E-14 1.2E-14 1.1E-17 Sr92 5.8E-15 5.8E-15 1.6E-22 Y90 9.1E-16 9.1E-16 1.1E-16 Y91m 6.6E-15 6.6E-15 7.1E-18 Y91 3.4E-15 3.4E-15 1.7E-16 Y92 5.6E-15 5.6E-15 2.2E-20 cale US460 SDAA 12.2-71 Revision 1

Air Space above Reactor CVCS Pump Room LWRS Degasifier Room Pool Airborne Radionuclide Airborne Concentration Airborne Concentration Concentration

(µCi/ml) (µCi/ml) (µCi/ml)

Y93 2.5E-15 2.5E-15 3.0E-18 Zr97 3.8E-15 3.8E-15 2.0E-17 Nb95 5.6E-15 5.6E-15 1.4E-13 Mo99 7.0E-12 7.0E-12 2.0E-13 Mo101 1.1E-13 1.1E-13 -

Tc99m 6.5E-12 6.5E-12 1.9E-13 Tc99 1.3E-16 1.3E-16 6.8E-18 Ru103 6.7E-15 6.7E-15 3.3E-16 Ru105 2.1E-15 2.1E-15 1.8E-20 Ru106 4.2E-15 4.2E-15 2.1E-16 Rh103m 6.6E-15 6.6E-15 3.2E-16 Rh105 4.5E-15 4.5E-15 8.3E-17 Rh106 4.2E-15 4.2E-15 -

Ag110 2.7E-15 2.7E-15 -

Sb124 1.0E-17 1.0E-17 5.0E-19 Sb125 7.4E-17 7.4E-17 3.8E-18 Sb127 3.7E-16 3.7E-16 1.3E-17 Sb129 4.3E-16 4.3E-16 3.6E-21 Te125m 1.1E-14 1.1E-14 5.4E-16 Te127m 4.1E-14 4.1E-14 2.1E-15 Te127 1.6E-13 1.6E-13 2.1E-15 Te129m 1.2E-13 1.2E-13 5.7E-15 Te129 1.5E-13 1.5E-13 3.6E-15 Te131m 3.8E-13 3.8E-13 5.4E-15 Te131 1.4E-13 1.4E-13 1.2E-15 Te132 2.8E-12 2.8E-12 8.7E-14 Te133m 1.8E-13 1.8E-13 -

Te134 2.3E-13 2.3E-13 -

Ba137m 1.3E-11 1.3E-11 -

Ba139 5.1E-15 5.1E-15 2.4E-28 Ba140 3.4E-14 3.4E-14 1.6E-15 La140 1.0E-14 1.0E-14 1.2E-15 La141 1.8E-15 1.8E-15 5.1E-21 La142 7.7E-16 7.7E-16 4.1E-28 Ce141 5.3E-15 5.3E-15 2.6E-16 Ce143 4.0E-15 4.0E-15 6.3E-17 Ce144 4.5E-15 4.5E-15 2.3E-16 Pr143 4.7E-15 4.7E-15 2.3E-16 Pr144 4.4E-15 4.4E-15 2.3E-16 Np239 8.4E-14 8.4E-14 2.2E-15 Na24 8.3E-12 8.3E-12 3.2E-14 Cr51 4.8E-13 4.8E-13 2.3E-11 Mn54 2.4E-13 2.4E-13 1.2E-11 Fe55 1.8E-13 1.8E-13 9.4E-12 cale US460 SDAA 12.2-72 Revision 1

Air Space above Reactor CVCS Pump Room LWRS Degasifier Room Pool Airborne Radionuclide Airborne Concentration Airborne Concentration Concentration

(µCi/ml) (µCi/ml) (µCi/ml)

Fe59 4.6E-14 4.6E-14 2.3E-12 Co58 7.0E-13 7.0E-13 3.5E-10 Co60 8.1E-14 8.1E-14 4.1E-12 Ni63 4.0E-14 4.0E-14 2.1E-12 Zn65 7.8E-14 7.8E-14 4.0E-12 Zr95 6.0E-14 6.0E-14 3.0E-12 Ag110m 2.0E-13 2.0E-13 1.0E-11 W187 4.2E-13 4.2E-13 4.3E-12 H3 3.2E-07 3.2E-07 2.3E-06 C14 3.2E-11 3.2E-11 1.9E-11 N16 - - -

Ar41 5.5E-08 5.5E-08 -

cale US460 SDAA 12.2-73 Revision 1

Radionuclide RCS Peak Concentration (µCi/g)

Kr83m 4.2E-01 Kr85m 4.5E-02 Kr85 5.9E+00 Kr87 1.8E-02 Kr88 5.1E-02 Kr89 1.2E-03 Xe131m 1.4E-01 Xe133m 2.1E-01 Xe133 1.0E+01 Xe135m 2.7E+00 Xe135 9.2E+00 Xe137 3.9E-03 Xe138 1.3E-02 Br82 1.1E-01 Br83 1.9E+00 Br84 3.2E+00 Br85 4.0E+00 I129 1.5E-06 I130 1.1E+00 I131 2.0E+01 I132 3.4E+01 I133 3.8E+01 I134 4.4E+01 I135 3.6E+01 Rb86m 5.2E-08 Rb86 3.0E-04 Rb88 6.0E-02 Rb89 2.4E-03 Cs132 6.0E-06 Cs134 4.3E-02 Cs135m 3.6E-05 Cs136 9.4E-03 Cs137 2.2E-02 Cs138 1.9E-02 P32 8.4E-10 Co57 6.4E-12 Sr89 3.9E-05 Sr90 6.0E-06 Sr91 2.0E-05 Sr92 1.1E-05 Y90 1.9E-06 Y91m 1.8E-05 Y91 5.6E-06 Y92 1.2E-05 Y93 4.3E-06 Zr97 6.3E-06 Nb95 9.7E-06 cale US460 SDAA 12.2-74 Revision 1

Radionuclide RCS Peak Concentration (µCi/g)

Mo99 1.1E-02 Mo101 4.3E-04 Tc99m 1.6E-02 Tc99 2.1E-07 Ru103 1.1E-05 Ru105 3.6E-06 Ru106 6.8E-06 Rh103m 2.1E-05 Rh105 7.7E-06 Rh106 1.4E-05 Ag110 1.2E-05 Sb124 1.6E-08 Sb125 1.2E-07 Sb127 6.1E-07 Sb129 7.6E-07 Te125m 1.8E-05 Te127m 6.7E-05 Te127 2.9E-04 Te129m 1.9E-04 Te129 3.9E-04 Te131m 6.2E-04 Te131 4.3E-04 Te132 4.6E-03 Te133m 3.9E-04 Te134 5.6E-04 Ba137m 4.2E-02 Ba139 1.0E-05 Ba140 5.6E-05 La140 2.3E-05 La141 3.2E-06 La142 1.5E-06 Ce141 8.6E-06 Ce143 6.5E-06 Ce144 7.3E-06 Pr143 7.7E-06 Pr144 1.4E-05 Np239 1.4E-04 Na24 1.4E-02 Cr51 7.7E-04 Mn54 4.0E-04 Fe55 3.0E-04 Fe59 7.5E-05 Co58 1.1E-03 Co60 1.3E-04 Ni63 6.6E-05 Zn65 1.3E-04 Zr95 9.7E-05 cale US460 SDAA 12.2-75 Revision 1

Radionuclide RCS Peak Concentration (µCi/g)

Ag110m 3.2E-04 W187 7.0E-04 H3 2.6E+00 C14 2.6E-04 N16 -

Ar41 1.0E-02 cale US460 SDAA 12.2-76 Revision 1

This section describes the incorporation of radiation protection design features in the NuScale Power Plant US460 standard design facilities. These include features to reduce both onsite and offsite exposures and to protect the environment. The facility incorporates design features using the guidance of U.S. Nuclear Regulatory Commission and industry documents (e.g., Regulatory Guide (RG) 8.8, RG 4.21, and NEI 08-08A) to ensure compliance with applicable regulations such as 10 CFR 20.1101, 10 CFR 20.1406 and 10 CFR 50.34.

3.1 Facility Design Features The following discussion contains specific system and facility design features that implement as low as reasonably achievable (ALARA) principles to the NuScale plant design. The design engineers incorporate these design features during the design process using applicable operating experience.

3.1.1 Equipment Design This section provides specific design features for component types that aid in maintaining occupational exposures ALARA.

3.1.1.1 Tanks The use of tanks with bottoms that slope toward outlets and, where practicable, providing built in spray features, spargers and eductors for mixing tank contents reduce radiation sources from sedimentation in tanks.

The tanks in the liquid radioactive waste (LRWS) and solid radioactive waste systems (SRWS) are stainless steel with sloped bottoms. The LRWS collection tanks and the solid radioactive waste storage tanks contain mixing eductors or spargers.

Tanks that are expected to contain radioactive contaminated fluids are of welded construction with a smooth interior finish that minimizes crevices and crud traps.

Tanks have overflow lines routed to receiving tanks, sumps or drains. Tank level alarms protect against overflow situations. The vents and drains associated with tanks containing contaminated fluids are processed by the building ventilation and the radioactive waste drain systems, respectively.

Tank materials are designed to be compatible with the service environment to reduce corrosion and leaks.

The pool cooling and cleanup system (PCWS) storage tank is located in a steel-lined catch basin with sufficient capacity to contain the tank volume along with its associated piping.

cale US460 SDAA 12.3-1 Revision 1

Remotely actuated valves are used to minimize personnel exposures, where practicable. Many valves are also located in valve galleries to provide additional shielding.

Double isolation valves are used at the interface between contaminated and non-contaminated systems to prevent cross-contamination.

Valves are designed to fail to the safe position upon a loss of power or air to the valve operator.

Full-port ball valves are used in the SRWS and the PCWS slurry lines to reduce potential crud traps.

Relief valves are provided to protect equipment and the relief discharge is directed toward the radioactive waste drain system (RWDS) to minimize the spread of contamination.

Reach-rods are used for valves in some applications.

Where practicable, valves are installed in the "stem-up" orientation.

Valves are designed to be repacked without removing the yoke or topworks.

3.1.1.3 Piping Construction and fabrication techniques employed by the following systems are used to exclude crevices and crud traps: LRWS, SRWS, PCWS, chemical and volume control system (CVCS), and radioactive waste drain system (RWDS). The SRWS deploys sloping, bends, and long radius elbows to minimize crud traps.

The LRWS and SRWS piping is provided with clean-in-place and flushing capabilities to reduce the buildup of crud and other contaminates. The CVCS and the PCWS have flushing connections to aid in the removal of contamination and reduce potential exposures to plant personnel.

Piping is designed for the lifetime of the facility.

System piping that contains radioactive fluids uses welded construction and smooth internal surfaces, as practicable. Whenever practicable, horizontal resin sluice lines are sloped to facilitate draining and prevent potential hot spots.

Embedded or underground piping is limited to the extent practical.

Underground pipes containing radioactive liquids, such as LRWS and PCWS piping, are enclosed within structured pipe chases or are double-walled. The CVCS, the process sampling system (PSS), and resin sluice pipes that are cale US460 SDAA 12.3-2 Revision 1

3.1.1.4 Pumps Pump leakage is reduced by using canned pumps whenever they are compatible with service needs.

The LRWS uses centrifugal pumps to minimize potential for crud traps.

Where appropriate, the design uses pumps with flanged connections for removal to low dose area for maintenance.

Drain connections on pump casings are provided where appropriate to reduce the radiation field during pump servicing.

3.1.1.5 Heat Exchangers Heat exchangers are designed for complete drainage before maintenance activities.

Flushing connections are provided for heat exchangers, where appropriate.

Heat exchangers use corrosion resistant materials to minimize need for replacement and internal surfaces are smoothed to be free of crevices.

Where practicable, heat exchangers are designed such that the contaminated fluid is on the tube side.

3.1.1.6 Instrumentation Whenever practicable, remote (in low dose areas) instruments and transmitters are used for systems with radioactive fluids.

Instruments in high radiation areas are designed to be easily removable.

Instrument sensing lines containing contaminated fluids are designed with back-flushing capability.

The locations and equipment specifications for seismic monitoring equipment (per RG 1.12) reduce the frequency and duration of testing, inspection or maintenance of seismic monitoring equipment.

3.1.1.7 Ventilation The Reactor Building HVAC system (RBVS) and the Radioactive Waste Building HVAC system (RWBVS) are once-through systems changing air volume from 0.5 to two times per hour for potentially contaminated areas. The design permits convenient inspection, maintenance and decontamination, and facilitates the replacement of critical components such as filters, fans, and cale US460 SDAA 12.3-3 Revision 1

where low levels of airborne contamination may be present toward areas of higher potential contamination. The exhaust ducts consist of straight runs and long radius elbows to reduce the buildup of contaminated particulate. The duct air velocity is kept at sufficiently high velocities to keep particulates suspended. Construction materials have smooth internal and external surface finishes to aid in decontamination. Back draft dampers are provided at each tank and equipment connection where required to prevent blowback in the event of an exhaust system trip.

Section 12.3.3 discusses ventilation systems.

3.1.1.8 Floor Drains Floor drains are provided for rooms and cubicles with components containing radioactive fluids that might leak or be spilled from process equipment or sampling stations.

Drain piping that is shielded by pipe chases, or otherwise shielded to reduce personnel exposure, include leak detection and confinement such that the fluid is contained.

3.1.1.9 Filters Filters for reactor coolant and potentially high-activity applications incorporate shielding, remote handling equipment, and radiation monitoring instrumentation to aid in maintaining personnel exposures ALARA.

Cartridge filter housings are designed with isolation valves, vents, and drains to allow the spent filter to be drained before maintenance activities.

Cartridge filter housings have minimal internal crevices to minimize the buildup of crud.

The design and configuration of filter housings and cartridges are standardized such that the same equipment and procedures can be used to change out spent filters.

3.1.1.10 Demineralizers Resin transfer operations are performed remotely through piping that is routed through a shielded pipe chase. Portions of piping that are not located in a shielded pipe chase are shielded to reduce the potential for worker exposure.

If necessary, administrative controls are enacted when high-activity resin transfers are planned to ensure that areas where high radiation may occur during the resin transfer are evacuated of personnel.

Demineralizers are designed and configured to allow for full drainage.

cale US460 SDAA 12.3-4 Revision 1

3.1.1.11 Charcoal Beds The redundant charcoal bed skids of the gaseous radioactive waste system (GRWS) are located in individual shielded cubicles.

Radiation detectors monitor the charcoal bed cubicles for gas leaks.

3.1.1.12 Sample Stations Radiation protection design features are incorporated into the design of sample stations for radioactive fluid. Primary coolant samples are routed to sample stations to minimize radiation dose from local sample points. Sample stations are shielded and are located in low-dose areas to minimize occupational exposures. Shielding of sample stations for primary coolant is achieved by routing sample lines in shielded pipe chases to the extent practicable. Sampling components that contain potentially radioactive fluids are located in shielded compartments or away from the sample panel to the extent practicable. Reactor coolant grab sample stations are equipped with vent hoods to reduce personnel exposure.

Sample stations contain flushing provisions with drains routed to the LRWS.

The laboratory and counting room are designed to provide low background radiation.

3.1.1.13 Material Selection Proper material selection is an important factor to balance component performance while reducing the amount of corrosion and activation products generated. The use of materials containing cobalt and nickel is minimized to reduce the quantity of activation products. Ni-Cr-Fe alloys, such as Inconel, have a high nickel content that can become Co-58 when activated. Production of Co-58 and Co-60 are reduced by utilizing low nickel and low cobalt bearing materials, to the extent practicable.

In limited situations, the selection of materials containing higher percentages of cobalt (e.g., hard face materials) or nickel (e.g., Alloy 690TT steam generator (SG) tubing) is preferable from a design standpoint. In these cases, the additional generation of activation products is balanced against component reliability to achieve the lowest overall personnel exposure. These types of materials are used only where operating experience suggests that it is the preferred option. Alloy 690TT is the material used for SG tubing because of its high resistance to corrosion.

Systems use stainless steel, or stainless steel clad, for components and piping where corrosion resistance and water quality is an important consideration (e.g., components that can come into contact with primary cale US460 SDAA 12.3-5 Revision 1

RG 1.143.

The reactor pressure vessel (RPV), control rod drive mechanisms (CRDMs),

and containment vessel (CNV) materials are predominately low alloy steels, clad with stainless steel, and austenitic stainless steels. The use of cobalt containing materials in contact with the primary coolant, such as Stellite, is limited to a small number of wear components such as CRDM latches, hard faces, springs and control rod assembly hub connection couplings (Haynes Alloy-25). Table 12.3-3 summarizes the typical cobalt content for materials and components.

3.1.2 Plant and Layout Design Features for as Low as Reasonably Achievable This section provides descriptions and examples of facility design features to reduce personnel exposures in accordance with the guidance of RG 8.8 and the ALARA principle.

3.1.2.1 Pipe Routing Whenever possible, pipes with radioactive fluids are routed through pipe chases or shielded areas, and away from pipes for "clean" services.

If pipes with radioactive fluids are routed near clean service pipes, provisions for isolation and draining of the radioactive pipes are provided.

Piping is designed to minimize "dead legs" and low points.

3.1.2.2 Valve Galleries Valve galleries are provided in several locations to protect plant operators from radiation exposures from process equipment. Floors are sloped towards local drain hubs to collect leakage. Concrete surfaces within the valve galleries are coated to facilitate decontamination.

3.1.2.3 Penetrations Penetrations through shield walls are minimized as much as practicable.

If penetrations through shield walls are necessary, the penetrations are designed to minimize streaming (e.g., with an offset) from a radiation source to accessible areas. If penetration offsets are not practical, then penetrations are either shielded or elevated above floor level. Shield wall penetrations are compensated to comply with the associated radiation zone map dose rates for normally accessible areas.

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Radioactive system components are located separately from "clean" components as much as practicable. Individual components of a radioactive system are typically located in separate shielded compartments with short piping runs between components. Where appropriate, shielded valve galleries are employed to allow system operation while shielding operators from high radiation components.

3.1.2.5 Lighting Adequate lighting is provided in radiation areas requiring access to facilitate surveillance and maintenance activities. Light fixtures are located in accessible areas to reduce replacement time. Multiple light fixtures are provided to reduce the need for immediate light bulb replacement. Emergency lighting fixtures reduce personnel exposures by permitting prompt egress from radiation areas if normal lighting fails.

3.1.2.6 Cubicles Shielded cubicles are provided for components containing significant radioactive sources. Cubicles are lined with stainless steel to a height necessary to contain the contents of the residing component plus piping drainage. In the event of a leak or spill, cubicle floors slope toward floor drains that are connected to sump tanks.

3.1.3 Radiation Zoning and Access Control 3.1.3.1 Normal Conditions The plant is analyzed for expected radiation levels resulting from normal operation. Because potential airborne exposures are possible in portions of the Reactor Building (RXB), principally due to off-gassing from the reactor pool and possible leaks or spills, airborne radiation zones are also developed.

Radiation levels are categorized along with anticipated personnel occupancy in Table 12.3-1, which tabulates the radiation zone categories and their access descriptions. Table 12.3-2 tabulates the airborne zone categories and their access descriptions.

Figures 12.3-1a through 12.3-1h show the normal operation radiation zones for the RXB. Table 12.3-4a and Table 12.3-4b list the areas that have the potential for airborne radiation in the RXB and the Radioactive Waste Building (RWB), respectively. Figure 12.3-2a through Figure 12.3-2c show the normal operation radiation zones for the RWB. The radiation zones are based on conservative assumptions related to source terms and are not intended to reflect the anticipated dose rates over the entire area.

Access to radiologically controlled areas (RCAs) is controlled by the facility's radiation protection staff. Access control facilities are provided to control the entrance and exit of personnel and materials into and out of the RCA. Access cale US460 SDAA 12.3-7 Revision 1

High radiation areas either are locked or have alarmed barriers. For areas that are not within lockable enclosures or other barriers, the area is barricaded and posted, and be provided with a visible warning light. Positive control is exercised over each individual entry when access to the area is required, and egress from the area is not impeded.

L Item 12.3-1: An applicant that references the NuScale Power Plant US460 standard design will develop the administrative controls regarding access to high radiation areas per the guidance of Regulatory Guide 8.38.

Very high-radiation areas are locked. Positive control is exercised over each individual entry when access to the area is required, and egress from the area is not impeded. Access to very high-radiation areas complies with guidance in RG 8.38. Based on the design and calculations, there are no very high-radiation areas.

L Item 12.3-2: An applicant that references the NuScale Power Plant US460 standard design will develop the administrative controls regarding access to very high radiation areas per the guidance of Regulatory Guide 8.38.

L Item 12.3-3: An applicant that references the NuScale Power Plant US460 standard design will specify personnel exposure monitoring hardware, specify contamination identification and removal hardware, and establish administrative controls and procedures to control access into and exiting the radiologically controlled area.

3.1.3.2 Accident Conditions Post-accident access is discussed in Section 12.4.1 and equipment qualification is addressed in Section 12.2.1 and Section 3.11. A radiation and shielding design review is performed of spaces around systems that may contain core damage source term materials, consistent with 10 CFR 50.34(f)(2)(vii). The resultant equipment protection from a core damage source term is addressed in Section 19.2. Area radiation monitors are provided to indicate the post-accident radiation levels, to monitor plant areas during the progression of a postulated accident, and provide local indication to plant personnel before area entry.

Section 7.1 contains additional information on post-accident monitoring (PAM) instrumentation.

3.2 Shielding 3.2.1 Design Bases The design function of shielding is to limit dose from plant radiation sources under normal operations and postulated accident conditions in accordance with General Design Criterion (GDC) 61, 10 CFR 50.34(f)(2)(vii), and 10 CFR 50.49.

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Shielding performance is in accordance with the following criteria:

  • dose limits of principal design criteria (PDC) 19 In addition, plant layout and shielding are used to limit equipment radiation doses to levels that are consistent with the assumptions used to demonstrate environmental qualification.

3.2.2 Design Considerations Shielding is provided for radioactive systems and components to reduce radiation levels commensurate with area personnel access requirements and ALARA principles. Section 12.3.1 describes the radiation zones and indicates the radiation levels for those plant areas.

Section 12.3.1 describes shielding design features including permanent shielding and separation of components that constitute substantial radiation sources, the use of shielded cubicles, labyrinths, and shielded entrances to minimize radiation exposures. The selection of shielding materials considers the ambient environment and potential degradation mechanisms. Temporary shielding is considered where it is impractical to provide permanent shielding for substantial radiation sources.

Consistent with RG 8.8, streaming of radiation into accessible areas through penetrations for pipes, ducts, and other shield discontinuities is reduced by using layouts that prevent alignment with the radiation source, placing penetrations above head height to reduce personnel exposures, and using shadow shields to attenuate radiation streaming.

Consistent with RG 8.8, shielding analysis employs accurate modeling techniques and conservative approaches in the determination of shielding thickness. Source terms, geometries, and field intensities are analyzed conservatively. In addition to normal conditions, source terms include transient conditions such as resin transfers.

The material used for a significant portion of plant shielding is concrete. For most applications, concrete shielding is designed in accordance with American National Standards Institute/American Nuclear Society (ANSI/ANS) 6.4-2006 (Reference 12.3-1). Table 12.3-5 and Table 12.3-6 show the shielding thicknesses assumed in the shielding analyses in plant buildings. In addition to concrete, other types of materials such as steel, water, tungsten, and polymer composites are considered for both permanent and temporary shielding. The use of lead is minimized.

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open doorways.

Shield floor plugs provide an equivalent radiation attenuation as the shield floor that contains the plug.

3.2.3 Calculation Methods The primary computer program to evaluate shielding is Monte Carlo N-Particle Transport Code (MCNP6) (Reference 12.3-2), which was developed by Los Alamos National Laboratory. The MCNP6 code is used for shielding calculations and for dose rate determinations.

Radioactive components in the RXB and RWB are modeled using MCNP6.

Section 12.2 describes the codes used to prepare source strength input data. A three-dimensional shielding model is constructed for radioactive components using structure, location, and equipment data. Source geometries and source term distributions and intensities are conservatively determined. In general, the component source geometries are modeled as cylindrical volumes that incorporate the full volume of the component.

Shielding credit and material selections for MCNP6 cells are conservatively applied. Credit is not taken for reinforcing steel bars in the concrete. Table 12.3-5 and Table 12.3-6 describe the credited shield barriers for the RWB and RXB in terms of nominal concrete equivalent thicknesses. The design provides equivalent density thicknesses for the barrier described using a variety of structural design solutions.

The reactor shielding calculations consider dose rates from fission neutrons, fission photons, and gamma output from buildup of radioisotopes in the reactor coolant. The NuScale Power Module (NPM) model is conservatively developed using methods similar to the building evaluations.

The fission neutron and fission photon output is based on a total power output of 250 MWt and energy spectra are described in Section 12.2. The gamma output from the reactor coolant is based on the reactor coolant isotopic inventory described in Section 12.2. In order to reduce complexity, some region densities (e.g., water and piping in the SGs) are homogenized in the MCNP model. This simplification does not result in significant differences in dose rates.

The shielding thicknesses are selected to reduce the aggregate dose rate from significant radiation sources in surrounding areas to values below the upper limit of the radiation zone depicted in the zone maps (Figure 12.3-1aFigure 12.3-2a though Figure 12.3-1h). Radiation zones are selected to facilitate personnel access for operation and maintenance.

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3.2.4.1 NuScale Power Module Biological shielding is provided above each NPM to allow personnel access.

The bioshield provides shielding using concrete, steel, and high-density polyethylene (HDPE).The bioshield design and the venting of radiolytically-generated gases from the HDPE shielding are described in Section 3.7.3.

Degradation of the polyethylene radiation shielding material could potentially occur if the exhaust ventilation provided for the reactor module bays does not maintain air temperatures under the bioshield less than 180°F (e.g., due to damper failure). Therefore, conditions in which the air temperature under the bioshield exceeds 180°F require an evaluation of the continued efficacy of the bioshield polyethylene material's radiation shielding properties.

The CNV, pool water, and pool wall provide shielding and attenuation. The pool wall thickness is used for attenuating radiation from the radiation sources associated with the NPM.

Pool wall penetrations into the reactor module bay are modeled using MCNP6, with the shield voids occupied by the piping, HVAC ducting, cabling, and insulation, as designed for the penetrations. The model includes filler materials between the void spaces following design standard specifications for shielding penetrations. Calculations performed to determine the doses in areas near the module bay shielding penetrations show that the US460 design provides adequate protection from radiation streaming. These penetration compensatory measures provide protection of equipment, and reduce exposures to workers and the public.

3.2.4.2 Main Control Room The dose rate in the main control room (MCR) during normal operations is negligible. The Control Building (CRB) room locations and elevations are shown in figures provided in Section 1.2. The CRB walls are designed to attenuate radiation from the RXB. As indicated by Table 15.0-10, the PDC 19 dose acceptance criteria for the control room are met for postulated accidents.

3.2.4.3 Reactor Building In general, the calculated dose rates in open areas and corridors of the RXB are less than five mrem/hr during normal operation as shown in the radiation zone maps (Figure 12.3-1aFigure 12.3-2a through Figure 12.3-1hFigure 12.3-2q).

The RXB includes systems that contain radioactive components. The major radiation sources in the RXB are associated with the NPM (Section 12.3.2.4.1), chemical volume and control system, the pool cooling cale US460 SDAA 12.3-11 Revision 1

Chemical and Volume Control System The CVCS contains radioactive ion exchangers, filters, and heat exchangers.

The CVCS components and piping are located below grade in the RXB as shown in the radiation zone maps.

The filters, ion exchangers, and heat exchangers are located in shielded cubicles. The knockout panels for accessing the CVCS ion exchangers provide equivalent shielding as the wall in which they are located. The CVCS filters and resin traps are accessible via removable floor shield plugs for maintenance purposes. The labyrinths in the cubicles provide shielding that significantly lowers the dose rates from areas adjacent to the radioactive component.

The CVCS is equipped with a resin transfer line used to transport resin slurry to the SRWS. The line is generically modeled in the RXB shielding model using the CVCS mixed-bed demineralizer transfer spectra, decayed for 48 hours5.555556e-4 days <br />0.0133 hours <br />7.936508e-5 weeks <br />1.8264e-5 months <br />. Resin transfers are planned evolutions to minimize operator exposure in accordance with ALARA principles.

Primary coolant piping in CVCS equipment rooms is shielded to minimize surveillance and maintenance dose rates. The reactor coolant system (RCS) discharge lines, which travel from the modules to the CVCS heat exchangers and purification equipment through a shielded pipe chase, are a radioactive source in the CVCS.

The CVCS design features that reduce radiation exposures are described in Section 9.3.4, Chemical and Volume Control System.

Pool Cooling and Cleanup Systems During normal conditions of operation, the pool cooling and cleanup system (PCWS) provides for water level control and temperature maintenance of the reactor pool, the refueling pool (RFP) and the spent fuel pool (SFP). It also removes impurities to reduce radiation exposures and to maintain water chemistry and clarity.

For purposes of radiation shielding, the pool cooling heat exchangers are a minimal source of external radiation, and do not require shielding.

The design features of the pool cooling and cleanup systems that reduce radiation exposures are described in Section 9.1.3.

Degasifier Room The LRWS degasifiers receive primary letdown and pressurizer vent flow from the CVCS. The degasifier contributes minor dose rates to the adjacent cale US460 SDAA 12.3-12 Revision 1

in the adjacent mechanical room.

Fuel Storage and Handling Systems The ultimate heat sink (UHS) is a safety-related pool of borated water that consists of the combined water volume of the reactor pool, RFP, and spent fuel pool. The UHS pool is located below grade in the RXB. The UHS provides shielding for the spent fuel assemblies in the SFP and the RFP as described in Section 9.1 and Section 9.2.5.

Shielding for radiation protection is maintained by the fuel handling equipment as described in Section 9.1.4.

Spent fuel is stored in the spent fuel pool, as described in Section 9.1. The radiation shielding provided by the pool water and the pool walls surrounding the fuel keeps radiation dose rates in the lower levels of the RXB within acceptance criteria.

3.2.4.4 Radioactive Waste Building The RWB houses significant radiation sources that belong to the radioactive waste processing systems, and pool cooling and cleanup system components. The specifics of these systems are discussed below. The radiation zone maps are located in Figures 12.3-2a through 12.3-2b.

Liquid Radioactive Waste System The LRWS is primarily located below grade in the RWB. The low-conductivity waste (LCW) and high-conductivity waste (HCW) sample tanks (two of each) contain LRWS water that is processed to comply with discharge or recycle requirements.

The LCW and HCW collection tanks are located in separate shielded compartments in the RWB. The respective transfer pumps for these tanks are located in shared compartments in the RWB. Each pair of transfer pumps is separated by sufficient space to allow room for temporary shielding, as well as space for tools, spare parts, and personnel.

Liquid radioactive waste demineralizers are located in a shared shielding labyrinth. Additional filtration systems are located on modular skids with integrated process shielding.

Additional shielding is modeled for the processing skids containing the LCW demineralizers as noted in Table 12.3-6.

Gaseous Radioactive Waste System cale US460 SDAA 12.3-13 Revision 1

compartments.

The redundant charcoal decay beds share a shielded compartment, separated by a shield wall. The decay beds are protected by a single guard bed that is separated by a shield wall.

The remaining GRWS components, consisting of gas heat exchangers (vapor condensers) and moisture separators, occupy a shared shielded compartment, separate from the decay beds and the guard bed, located in the RWB.

Solid Radioactive Waste System The SRWS is located in the RWB. The SRWS components are generally located in separate, shielded compartments.

The two phase separator tanks and the two spent resin tanks are located in individual shielded compartments. The respective transfer pumps for these tanks are located in shared compartments in the RWB. Each pair of transfer pumps is separated by sufficient space to allow room for temporary shielding, as well as space for tools, spare parts, and personnel.

The SRWS consists of both Class A and Class B/C waste storage areas. A Class A waste package storage area is located at grade level. The Class A high integrity container (HIC) and Class B/C HIC storage area is located on the lower level. Access to the HIC storage area is through floor shield plugs.

Additional shielding is modeled for the HIC process shield, and an external shield is modeled outside a penetration through the HIC storage room shield wall, as noted in Table 12.3-6.

Pool Cooling and Cleanup The PCWS demineralizers and filters are located in shielded cubicles in the RWB. The dose rates in surrounding areas are acceptable for operations or maintenance activities.

3.3 Ventilation The plant HVAC systems are designed to provide a controlled environment for personnel and equipment during normal operation. In areas subject to airborne radioactivity, the ventilation systems are designed to collect, process, and direct airflow to processed exhausts (Section 9.4, HVAC Systems). This section discusses the radiation control considerations of the HVAC systems design.

3.3.1 Design Objectives Design objectives for the plant HVAC systems include the following:

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and within the limits specified in 10 CFR 20. The airborne radioactivity released during normal plant operations are also maintained ALARA and within the limits of 10 CFR 20, Appendix B, Table II.

  • During normal plant operations, the dose from airborne radioactive material exposure in unrestricted areas is maintained ALARA and within the limits specified in 10 CFR 20.1301 and 10 CFR 50, Appendix I.
  • The dose to the control room personnel does not exceed the limits specified in PDC 19 following the design basis accidents described in Chapter 15.

3.3.2 Design Features to Minimize Personnel Exposure from Heating, Ventilation, and Air Conditioning Equipment The design of the building ventilation systems maintain a negative pressure where required with respect to the outside environs and create air flow inside the building from areas of low airborne potential contamination to areas of higher airborne potential contamination.

Other design features that minimize radiation exposures to personnel are listed below.

  • The design of the plant ventilation systems incorporates the guidance of RG 8.8.
  • Ventilation fans and filters are provided with adequate access space to permit servicing with minimum personnel radiation exposure. The HVAC system is designed to allow rapid replacement of components. Filter-adsorber unit performance complies with the recommendations of RG 1.140.
  • Ventilation ducts are designed to minimize the buildup of radioactive contamination within the ducts.
  • Access to ventilation systems in potentially radioactive areas can result in personnel exposure during maintenance, inspection, and testing. Equipment is located in low-dose areas as much as practicable, with most equipment being located outside of rooms that contain significant radiation sources. The outside air supply units and building exhaust system components have adequate work space provided around each unit for anticipated maintenance, testing, and inspection.

3.3.3 Reactor Building Heating, Ventilation, and Air Conditioning System During normal operation, the RBVS services the areas inside the RXB by providing conditioned and filtered outside air. The exhaust from the spent fuel pool area is filtered by a high-efficiency particulate air (HEPA) filter. If the spent fuel pool exhaust radiation monitors detect radioactivity above their setpoints, the exhaust flow from the spent fuel pool area is diverted to go through an additional HEPA filter and charcoal adsorbers. Section 9.4.2, Reactor Building HVAC, contains additional details.

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activities.

Heating, ventilation, and air conditioning equipment drains are routed to the RWDS.

The design provides adequate space for temporary shielding to minimize personnel exposures during maintenance of ventilation equipment, including filters, inspection, and testing. In addition, the filter units have design features that minimize the time required for filter changes.

3.3.4 Radioactive Waste Building Heating, Ventilation, and Air Conditioning System The RWBVS serves the RWB as a once-through system. Outside air is introduced by the main supply air handling unit (AHU) and is exhausted through the RBVS exhaust system. The main supply AHU contains both low and medium efficiency outside air filters. Supply air from the main RWBVS is distributed throughout the RWB. Exhaust air is collected and conveyed to the RBVS general area exhaust subsystem and exhausted through the main stack. The RWBVS maintains airflow from areas of lesser potential contamination to areas of greater potential contamination. The RWBVS also maintains the RWB atmosphere at a slight negative pressure with respect to the outside. Section 9.4.3, Radioactive Waste Building HVAC, contains additional details.

3.3.5 Normal Control Room Heating, Ventilation, and Air Conditioning System During normal operations, the normal control room HVAC system (CRVS) supplies conditioned air to the CRB, including the control room envelope (CRE),

the technical support center, and the other areas of the CRB with outside air that is filtered (low and medium efficiency) to maintain a suitable environment for personnel and equipment. The CRVS is designed to maintain a positive pressure inside the CRB with respect to adjacent spaces. Section 9.4.1, Control Room Area Ventilation System, contains additional details.

If a high radiation indication is received from an outside air intake radiation monitor, the supply air is routed through the CRVS filter unit, which provides HEPA and charcoal filtration. The CRVS is designed to maintain operator doses in the MCR and technical support center within PDC 19 limits.

If power is not available, or if a high radiation indication is received from the radiation monitors in the CRE supply duct, the CRE isolation dampers close and the control room habitability system (CRHS) is initiated.

3.3.6 Control Room Habitability System The CRHS uses a set of compressed air storage bottles to supply the CRE with breathing air in the event of an emergency. Upon receiving an initiation signal, the CRHS supplies the CRE with clean air and maintains the CRE at a positive cale US460 SDAA 12.3-16 Revision 1

3.4 Area Radiation and Airborne Radioactivity Monitoring Instrumentation The fixed area radiation monitors (ARMs) are placed in selected general plant locations. They provide local and MCR indication of gamma radiation at each location and provide an alarm function both locally and in the MCR when predetermined thresholds are exceeded.

The ARMs located under the bioshield for each NPM provide normal and post-accident indication of containment gamma radiation within the bioshield envelope during normal and accident conditions. The monitors detect fuel cladding breach under potential core damaging accident conditions. Section 9.3.2, Process Sampling System, discusses the use of ARMs.

The ARMs located adjacent to the CVCS reactor coolant filters provide indication of radioactive material buildup to allow the operator to remove them from service for maintenance before reaching predetermined thresholds for radiation. Area radiation monitoring design features, quality group, seismic requirements, and functions are described below. The CVCS design features, functions, and flow paths are described in Section 9.3.4.

The ARMs located in the spent fuel pool area provide the same functions as the general plant location monitors, and in addition monitor the fuel storage and handling areas. Additionally, a local ARM is mounted on the refueling bridge with local and MCR alarm function that monitors refueling activities.

The fixed continuous air monitors (CAMs) are placed in selected general plant locations. They provide local and MCR indication of airborne radioactivity within the plant environs at each location and provide an alarm function both locally and in the MCR when predetermined thresholds are exceeded.

The CAM for the GRWS provides an additional function: detection of GRWS process gas leakage. The GRWS continuous airborne radiation monitor function is described in Section 11.3, Gaseous Waste Management System.

3.4.1 Design Bases The area and airborne radiological monitoring equipment is designed to meet the following design basis requirements:

  • provide monitoring of area and airborne radiation levels in fuel storage and handling areas, and radioactive waste management systems to detect excessive radiation levels (GDC 63)
  • provide monitoring of plant area and airborne radiation levels such that worker dose can be maintained ALARA conforming to 10 CFR 20.1101(b) cale US460 SDAA 12.3-17 Revision 1

10 CFR 20.1201 and 10 CFR 20.1202

  • provide monitoring of airborne radiation levels such that area dose rate can be monitored, in part conforming to 10 CFR 20.1203
  • provide monitoring of airborne radioactive materials in work areas conforming to 10 CFR 20.1204
  • provide monitoring of plant area and airborne radiation levels such that contaminated system leaks can be detected and addressed in a timely manner, in part conforming to 10 CFR 20.1406
  • provide monitoring of plant area and airborne radiation levels such that effective surveys of these parameters can be maintained, conforming to 10 CFR 20.1501
  • provide monitoring of plant area and airborne radiation levels for a broad range of routine and accident conditions, conforming to 10 CFR 50.34(f)(2)(xxvii)
  • provide radiation monitoring in storage and associated handling areas when fuel is present to detect excessive radiation levels and to initiate appropriate safety actions, conforming to 10 CFR 50.68(b)(6).

3.4.2 Fixed Area Radiation Monitoring Instrumentation The fixed ARMs and associated instrument and controls platforms provide indication and archiving function to the MCR, furnishing information that can supplement radiological surveys, meet reporting requirements, and inform workers of radiological conditions before accessing monitored areas, thus providing the capability for plant staff to meet the requirements of 10 CFR 20.1501.

The ARMs provide both indication and alarm functions to the local plant area, the MCR, and, for selected areas, the waste management control room. The indication ensures operator and worker awareness of changing radiological conditions that could indicate system leakage or component malfunction, and provides a warning to plant personnel before entry into the affected areas. Where appropriate, local visual alarms are provided outside of the monitored area to ensure worker awareness before entry into the affected area.

The above design features conform to the requirements of 10 CFR 20.1101(b),

10 CFR 20.1201, 10 CFR 20.1406, and 10 CFR 50.34(f)(2)(xxvii).

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been determined to be abnormal. The alarm setpoints are adjusted to values that are low enough for the minimum detectable activity anticipated and high enough not to give false alarms. Alarms are designed such that they do not reset without operator action. The radiation monitor remains operable when the alarm setpoint is exceeded.

Meters, alarm indicators, and audible devices are designed so plant personnel can quickly determine the status of each radiation channel. These functions ensure personnel working in the vicinity are able to determine easily the status of an ARM channel when in the vicinity of the local indication devices.

Fixed ARM placement conforms to the criteria for selection and placement of the area radiation monitoring instrumentation contained within ANSI/ANS-HPSSC-6.8.1-1981, "Location and Design Criteria for Area Radiation Monitoring Systems for Light Water Nuclear Reactors" (Reference 12.3-4). Area radiation detectors are located in those areas that are normally accessible and require entry, exit, or both to monitor for purpose of occupational radiation protection. To the extent practicable, detectors are located to best measure the representative exposure rates within a given area or specified location.

The following criteria are considered for detector placement.

  • Areas that are normally accessible and where changes in normal plant operating conditions can cause significant increases in exposure rates above those expected for the areas.
  • Areas that are normally or occasionally accessible and where significant increases in exposure rates might occur because of operational transients or maintenance activities.
  • Areas where shielding of the detector by equipment or structural materials are avoided to ensure correct monitor response to increases in exposure rates within a specific area
  • Environmental conditions under which the monitor operates consider the range of temperature, pressure and humidity of areas where the detector and electronics are located.
  • The electronic controls for the monitors are placed in the lowest dose area practicable to provide maintenance access in an unobstructed area.

The fixed ARM indicating ranges consider the design maximum dose rate of the radiation zone in which they are located and the maximum dose rate for anticipated operational occurrence and accident conditions. Multiple-range devices are used for applications where a single monitoring range is not sufficient to envelope the entire anticipated indication requirement. The range of the radiation monitor is chosen so that the upper end of the scale is high enough to ensure on-scale reading for exposure rates far greater (approximately two decades) than the expected peak exposure rate, and the low end is at the lower cale US460 SDAA 12.3-19 Revision 1

The ARMs employ a simple and robust design to minimize routine maintenance.

The radiation monitors allow for periodic and corrective maintenance during normal operation, accident conditions, and outages. The fixed ARM calibration methods are performed on an annual basis or in alignment with the manufacturer's recommendations. Each area radiation monitor may have a check source that is used to provide operability checks.

Consumable filter media and cartridges for the collection of airborne radioactive particulates and iodine are replaced on a periodic basis. The periodicity of filter and cartridge replacements is dependent upon vendor recommendations and plant operating experience. Replacement of consumable filter media and cartridges shall be part of routine maintenance with proper procedures in place.

Selected ARMs support accident condition response and are PAM system variables, as described in Table 12.3-8 and Table 7.1-7. The fixed ARMs used for PAM have ranges that consider the maximum calculated accident levels and are designed to operate effectively under the environmental conditions caused by an accident. These monitors conform to the guidance of RG 1.97.

The ARMs located under the bioshield for each NPM detect fuel damage under accident conditions, and are considered PAM system B, C, and F variables.

Monitors are located at the top of each NPM beneath the bioshield. The radiation monitors under the bioshield are environmentally qualified to survive an accident and perform their design functions. The instruments are designed to respond to gamma radiation over the energy range of at least 60 keV to 3 MeV, with a dose rate response accuracy within a factor of two over the entire range. These monitors also meet the applicable requirements of Institute of Electrical and Electronics Engineers Standard 497-2016 "Criteria for Accident Monitoring Instrumentation for Nuclear Power Generating Stations" (Reference 12.3-7). By the use of independent vendors using software that is independent, the design configuration meets the requirements of Institute of Electrical and Electronics Engineers Standard 497-2016, Section 6.2, Common Cause Failure.

Fixed area radiation monitoring data are capable of being supplied to the NRC Operations Center through the connection to emergency response system via a secure direct electronic data link in the event of an emergency. The Connection to emergency response systems is discussed in Section 7.2.13.

Electrical power to the ARMs is provided by the following systems.

  • Fixed ARMs that are classified as a Type B PAM variable receive power from the augmented DC power system (EDAS).
  • Fixed ARMs that are classified as a Type C PAM variable receive power from the (EDAS) DC power system.
  • Fixed ARMs that are classified as a Type E PAM variable receive power from the normal DC power system (EDNS).

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The methodology for inspections, tests, analyses, and acceptance criteria associated with the fixed area radiation monitors are described in Section 14.3.

Table 12.3-10 provides information about the ARMs used including location and design features such as the type of radiation monitored and the associated principle isotope(s), instrument ranges, and the identification of monitors that serve a PAM function.

L Item 12.3-4: An applicant that references the NuScale Power Plant US460 standard design will develop the processes and programs necessary for the implementation of 10 CFR 20.1501 related to conducting radiological surveys, maintaining proper records, calibration of equipment, and personnel dosimetry.

3.4.3 Airborne Radioactivity Monitoring Instrumentation The fixed continuous airborne radiation monitors and their associated instrument and controls platforms provide indication and archiving function to the MCR, furnishing information that can supplement radiological surveys, meet reporting requirements, and inform workers of radiological conditions before accessing monitored areas, thus providing the capability for plant staff to meet the requirements of 10 CFR 20.1501.

The CAMs provide both indication and alarm functions to the local plant area, the MCR, and, for selected areas, the waste management control room. These functions ensures operator and worker awareness of changing radiological conditions that could indicate system leakage or component malfunction, and provides a warning to plant personnel before entry into the affected areas. Where appropriate, local visual alarms are provided outside of the monitored area to ensure worker awareness before entry into the affected area.

The above design features conform to the requirements of 10 CFR 20.1101(b),

10 CFR 20.1201, 10 CFR 20.1406, and 10 CFR 50.34(f)(2)(xxvii).

Selected fixed CAMs that support accident condition response and are PAM system variables, as described in Table 12.3-8 and Table 7.1-7. The fixed CAMs for PAM system have ranges that consider the maximum calculated accident levels and are designed to operate effectively under the environmental conditions caused by an accident. The CAMs used to fulfill PAM system functions conform to the guidance of RG 1.97.

Fixed CAM data are capable of being supplied to the NRC Operations Center through the connection to emergency response system via a secure direct electronic data link in the event of an emergency. Section 7.2 discusses the connection to emergency response system.

Alarm setpoints are established to alert plant personnel when airborne radioactivity in a specific location reaches levels that have been determined to be cale US460 SDAA 12.3-21 Revision 1

Alarms are designed such that they do not reset without operator action. The radiation monitor remains operable when the alarm setpoint is exceeded.

Meters, alarm indicators, and audible devices are designed so plant personnel can quickly determine the status of each radiation channel. These functions ensure personnel working in the vicinity are able to determine easily the status of fixed CAMs when in the vicinity of the local indication devices.

Fixed CAM placement and selection conforms to the criteria contained within ANSl/HPS N13.1-2011, "Sampling and Monitoring Releases of Airborne Radioactive Substances from the Stacks and Ducts of Nuclear Facilities" (Reference 12.3-8) and RG 8.25. The following criteria are considered for monitor placement:

  • Areas that are normally accessible and where changes in normal plant operating conditions can cause significant increases in airborne radioactivity above those expected for the areas.
  • Areas that are normally or occasionally accessible and where significant increases in airborne radioactivity might occur because of operational transients or maintenance activities.
  • Optimal location to measure the increase in airborne radioactivity within a specific area, including leak detection functions for systems that convey process gases that contain radionuclides and hydrogen.
  • Provide maintenance access in an unobstructed area. The electronic controls for the monitors are placed in the lowest dose area practicable.
  • Proximity of the airflow path that is as close as practical to potential release points.

The range of the fixed CAMs is chosen so that the upper end of the scale is high enough to ensure on-scale reading for exposure rates far greater (approximately two decades) than the expected peak exposure rate, and the low end is at the lower end of the expected exposure rate range but provide an on-scale value for the range of the instrumentation selected.

The fixed CAM calibration methods and frequency are in accordance with manufacturer recommendations and consider the rate at which instrument components age or become damaged. The calibrations are performed in a manner consistent with ALARA principles and follow the guidance of EPRI report TR-102644 Revision 1, "Calibration of Radiation Monitors at Nuclear Power Plants" (Reference 12.3-5). Recalibrations are performed on the detectors after maintenance or replacement of components that affect calibration. Radiation detectors used to satisfy PAM requirements are provided a means of calibration and testing the operability of each instrument channel during plant operation.

Functional testing of the fixed CAMs is performed to verify the operability of the channel, including alarm functions in accordance with manufacturer's requirements and using the guidance of EPRI report TR-104862, Revision 2, cale US460 SDAA 12.3-22 Revision 1

returned to the non-test mode upon deactivation or loss of power to the monitor.

The following systems provide electrical power to the fixed CAMs.

  • Fixed continuous airborne radiation monitors that are classified as a Type E PAM variable receive power from the EDNS.
  • Fixed continuous airborne radiation monitors that are not used for PAM variables receive power from the EDNS.

The methodology for inspections, tests, analyses, and acceptance criteria associated with the fixed area radiation monitors are described in Section 14.3.

Table 12.3-9 provides information about the fixed airborne monitors used including location and design features such as the type of radiation monitored and the associated principle isotope(s), instrument ranges, and the identification of which monitors serve a PAM function.

3.4.4 Portable Airborne Monitoring Instrumentation L Item 12.3-5: An applicant that references the NuScale Power Plant US460 standard design will develop the processes and programs necessary for the use of portable airborne monitoring instrumentation, including accurately determining the airborne iodine concentration in areas within the facility where plant personnel may be present during an accident.

3.5 Dose Assessment Section 12.4, Dose Assessment.

3.6 Minimization of Contamination and Radioactive Waste Generation Design features incorporated into the plant, combined with operational programs, are provided to comply with 10 CFR 20.1406, and the guidance of RG 4.21, to minimize contamination of the facility and the environment, minimize the generation of radioactive waste, and facilitate decommissioning. The design of the facility is evaluated in a systematic and risk-informed fashion against the design objectives below to determine the design features necessary for plant structures, systems, and components (SSC).

The SSC that have potential to contain contaminated fluids have design features to reduce the likelihood of leaks, provisions to detect leaks that do occur and reduce the spread of contamination, thus reducing the need for decontamination and the generation of waste. Table 12.3-11 provides a list of structures and systems that have been evaluated for design features consistent with RG 4.21. Table 12.3-11 through Table 12.3-40 provide the results of the system evaluations.

cale US460 SDAA 12.3-23 Revision 1

Regulatory Guide 4.21 addresses each phase of the NuScale Power Plant lifecycle, from the early design phases through decommissioning. The discussion of the lifecycle phases is separated into four design phase objectives and two operational objectives. Application of these six objectives demonstrates compliance with 10 CFR 20.1406 requirements.

The design features in the NuScale facility include measures to minimize and detect leakage, reduce radioactive waste generation, and facilitate decommissioning. These measures address the following objectives:

  • Objective 1 - Minimize the potential for leaks and spills to prevent the spread of contamination.
  • Objective 2 - Provide sufficient leak detection capability to support timely leak identification from appropriate SSC.
  • Objective 3 - Reduce the likelihood of cross-contamination, the need for decontamination and waste generation.
  • Objective 4 - Facilitate eventual decommissioning through design practices.

In combination with the four design related objectives listed above, two operational objectives are included to fully demonstrate compliance:

  • Objective 5 - Operational and programmatic considerations
  • Objective 6 - Site Radiological Environmental Monitoring 3.6.1.1 Design Considerations to Minimize Leaks and Contamination -

Objective 1 Facility contamination can be spread by leaks and spills of fluids containing radioactive material. To reduce the potential for these leaks and spills, the following design features include:

  • proper selection of materials that are commensurate with the SSC service conditions to reduce the effects of corrosion, temperature, pressure, and more.
  • providing walls, dikes, drains, sloped floors, and other leak collection features to contain leaks and spills from SSC containing contaminated, or potentially contaminated, liquids
  • minimize the use of buried or embedded piping and drains without the concurrent use of double-walled pipe with leak detection capability
  • proper design of components regarding properly sized overflow lines and catch basins or drip pans that are routed to drains
  • use proven technologies with the proper quality controls and compliance to applicable codes and standards cale US460 SDAA 12.3-24 Revision 1

Prompt leak detection from SSC provides the opportunity for an appropriate response to prevent unintended spread of radioactive contamination. The following design features are incorporated, where appropriate, in the facility design:

  • leak detection instrumentation for specific plant SSC
  • floors designed with drains and leak detection equipment
  • drainage collection provisions with leak detection equipment
  • liquid- and moisture-detection instruments with appropriate sensitivity
  • provisions for periodic calibration and maintenance of leak detection instrumentation
  • sufficient space for access to assess detected leaks and allow operator response
  • area and airborne radiation monitors
  • trenches or guard pipes with leak detection capabilities 3.6.1.3 Design Considerations for Reduction of Cross-Contamination, Decontamination and Waste Generation - Objective 3 Design features are incorporated to reduce the potential for cross-contamination, the need for decontamination, and radioactive waste generation. These kinds of design considerations include
  • separation of components according to their contamination level and characteristics.
  • the ability to sufficiently contain, isolate, and hold contamination until operator responses can be initiated.
  • smooth and cleanable surfaces on SSC to ease decontamination.
  • flushing capabilities for appropriate systems to be able to clean in place.
  • an on-site decontamination facility.
  • design for ventilation flow to be from lower contaminated areas to higher contaminated areas.
  • double isolation valves between clean and contaminated systems.
  • the use of butt welds, full ported valves and diaphragm seals, where appropriate, to minimize crud traps.

3.6.1.4 Design Considerations for Decommissioning - Objective 4 The following facility design features are included, as appropriate:

  • use of modular construction
  • minimizing the use of buried or embedded piping and components cale US460 SDAA 12.3-25 Revision 1
  • component designs to include, as appropriate, lifting lugs, easily removable insulation, and sufficient means for removal 3.6.1.5 Operational and Programmatic Considerations - Objective 5 The following procedural measures are employed:
  • periodic review of site procedures and programs to ensure adherence by, and training of, plant personnel and to verify proper updates to reflect plant modifications (Reviews are also conducted after leak or spill events to verify the adequacy of the associated programs and procedures).
  • site procedures and programs include measures to control contamination from potential leaks and spills, including monitoring, surveillances, and preventative maintenance.
  • proper documentation of the facility design, construction, modifications, and operations, including site contamination events.

3.6.1.6 Site Radiological Environmental Monitoring - Objective 6 A conceptual site model is developed that

  • characterizes the site's geology and hydrology and evaluates the predominant ground water flow characteristics and gradients.
  • identifies potential pathways for ground water migration to offsite locations.
  • evaluates the impact of construction upon the site's hydrogeological characteristics.
  • forms part of the basis for a site radiological monitoring program for ground water migration of potential releases.

L Item 12.3-6: An applicant that references the NuScale Power Plant US460 standard design will develop the processes and programs associated with Objectives 5 and 6, to work in conjunction with design features, necessary to demonstrate compliance with 10 CFR 20.1406, and the guidance of Regulatory Guide 4.21.

3.7 References 12.3-1 American National Standards Institute/American Nuclear Society, "Nuclear Analysis and Design of Concrete Radiation Shielding for Nuclear Power Plants," ANSI/ANS 6.4-2006, La Grange Park, IL.

12.3-2 Monte Carlo N-Particle Transport Code System Including MCNP6. 1, MCNP5-1.60, MCNPX-2.7.0 and Data Libraries [Computer Program]. Oak Ridge National Laboratory Radiation Safety Information Computational Center (RSICC) Computer Code Collection (CCC-740), Oak Ridge, TN.

cale US460 SDAA 12.3-26 Revision 1

ANSI/ANS 6.1.1-1977, La Grange Park, IL.

12.3-4 American National Standards Institute/American Nuclear Society, "Location and Design Criteria for Area Radiation Monitoring Systems for Light Water Nuclear Reactors," ANSI/ANS/HPSSC-6.8.1-1981, LaGrange Park, Il.

12.3-5 Electric Power Research Institute, "Calibration of Radiation Monitors at Nuclear Power Plants," EPRI #102644, EPRI, Palo Alto, CA, 2005.

12.3-6 Electric Power Research Institute, "Area and Process Radiation Monitoring System Guide," EPRI #104862, EPRI, Palo Alto, CA, 2003.

12.3-7 Institute of Electrical and Electronics Engineers, "Criteria for Accident Monitoring Instrumentation for Nuclear Power Generating Stations,"

IEEE Standard 497-2016, New York, NY.

12.3-8 American National Standards Institute/Health Physics Society, "Sampling and Monitoring Releases of Airborne Radioactive Substances from the Stacks and Ducts of Nuclear Facilities," ANSI/HPS N13.1-2011, Washington, DC.

12.3-9 Oak Ridge National Laboratory, "SCALE: A Comprehensive Modeling and Simulation Suite for Nuclear Safety Analysis and Design, ORNL/TM-2005/39, Version 6, Vols. I-III, ORNL/TM-2005/39, Version 6.1, June 2011.

cale US460 SDAA 12.3-27 Revision 1

Scale Final Safety Analysis Report one Designation Restriction Radiation Limit Description Regulatory Requirement Unrestricted Zones 0 Unrestricted area None 0.05 mrem/hr 0.5 µSv/hr Areas of the plant that can be 10 CFR 20.1301(a)(2) occupationally occupied without exceeding annual dose limits for members of the public.

Controlled Zones I Controlled area Limited > 0.05 mrem/hr > 0.5 µSv/hr Areas of the plant that can be 10 CFR 20.1502(a)(1) occupancy 0.25 mrem/hr 2.5 µSv/hr occupationally occupied without exceeding personnel radiation monitoring requirements (10% of 10 CFR 20.1201(a) limit).

Restricted Zones II Controlled area Personnel > 0.25 mrem/hr > 2.5 µSv/hr Areas of the plant that can be 10 CFR 20.1201(a) radiation 2.5 mrem/hr 0.025 mSv/hr occupationally occupied without monitoring exceeding the annual occupational dose limit of 5 rem (0.05 Sv).

III > 2.5 mrem/hr > 0.025 mSv/hr Areas of the plant that require limited 10 CFR 20.1201(a) 5 mrem/hr 0.05 mSv/hr access to ensure compliance with the annual occupational dose limit of 5 rem (0.05 Sv).

IV Radiation area Posting > 5 mrem/hr > 0.05 mSv/hr Areas of the plant that require posting as 10 CFR 20.1902(a) required 100 mrem/hr 1 mSv/hr radiation areas.

V High Radiation area1 Access > 100 mrem/hr > 1 mSv/hr Areas of the plant that require controlled 10 CFR 20.1601 restriction 1 Rad/hr 10 mGy/hr access and posting as high radiation 10 CFR 20.1902(b)

Radiation Protection Design Features areas.

VI Locked high-radiation > 1 Rad/hr > 10 mGy/hr area1 500 Rad/hr 5 Gy/hr VII Very high-radiation > 500 Rad/hr > 5 Gy/hr Areas of the plant that require controlled 10 CFR 20.1602 area access and posting as very high 10 CFR 20.1902(c) radiation areas.

e high-radiation area designation is split for administrative purposes into two zones. This is to provide the opportunity for additional controls to be used for s with radiation dose rates above 1 Rad/hr.

Scale Final Safety Analysis Report Zone Designation Restriction Radiation Limit Description Regulatory Requirement Unrestricted Zones 0 Unrestricted area None 0.01 DAC1 Areas that can be maintained as uncontrolled 10 CFR 20 App. B, Table 2 because radionuclide concentrations can be notes inhaled continuously without exceeding public dose limit.

Controlled Zones I Controlled area Limited occupancy > 0.01 DAC Areas of the plant that can be continuously 10 CFR 20.1502(b)(1) 0.1 DAC occupied without personnel radiation monitoring required (10% of applicable ALIs2).

Restricted Zones II Controlled area Personnel radiation > 0.1 DAC Areas of the plant that can be occupationally 10 CFR 20.1003 monitoring 0.3 DAC occupied without exceeding the airborne 10 CFR 20.1502(b)(1) radioactivity area limit requiring respiratory protective equipment.

III > 0.3 DAC Areas of the plant that require respiratory 1 DAC protective equipment.

IV Airborne radioactivity area Posting required > 1 DAC Areas of the plant that require posting as 10 CFR 20.1003 airborne radioactivity areas. 10 CFR 20.1902(d) s:

AC = derived air concentration LI = annual limit on intake Radiation Protection Design Features

Material or Application Maximum Weight Percent of Cobalt enitic stainless steel weld filler metals (including cladding) 0.05 enitic stainless steel base materials for large forgings (typically include 0.05 e austenitic stainless steel forgings for RPV, RVI, and CNV) r austenitic stainless steel base materials not covered elsewhere in this 0.15 e

ctor vessel internal core reflector blocks 0.05 r-Fe base metal and weld filler metals (except Alloy 690 SG tubing 0.05 w) y 690 SG tubing 0.014 max average per NuScale power module (NPM), with no single heat exceeding 0.020 637, N07718 (Aloy 718) bolting 0.05 r small products in contact with primary coolant Not limited, 0.2 target M internals springs in contact with primary coolant (Inconel X-750) 1 cale US460 SDAA 12.3-30 Revision 1

Location & Room # (Note 1) Description Source of Airborne Radioactive Material ation 25-0 LRWS degasifier pump rooms Primary coolant, CVCS 35 & 036) letdown ation 25-0 CVCS demineralizer valve Primary coolant 06, -009, -012, -024, -027, & 030) gallery/labyrinth ation 40-0 CVCS recirculation pump Primary coolant 08, through -116,& 122 through -130) rooms and valve galleries ation 40-0 LRWS degasifier tank cubical Primary coolant, CVCS 34 & 037) letdown ation 55-0 CVCS heat exchanger utility Leaked airborne from CVCS 06 & 215) areas valve galleries ation 55-0 Module heatup system (MHS) Primary coolant

13) equipment room ation 70-0 PSS primary sampling panels Primary coolant
30) room ation 70-0 Pool cooling and cleanup Pool water
04) system equipment aisleway ation 70-0 CFDS pump utilities area Pool water 17) ation 85-0 Hot lab Primary coolant samples 32) ation 100-0 MS galleries Vented RCS leaks into CNV 07 & 512) ation 100-0 Reactor pool area Pool evaporation 42) 1: Figure 1.2-8 through Figure 1.2-18 depict room locations.

cale US460 SDAA 12.3-31 Revision 1

Material Location & Room # (Note 1) Description Source of Airborne Radioactive Material ation 70-0 PCWS filter rooms Pool water 29 & 030) ation 70-0 PCWS demineralizers and Pool water, PCWS 31 & 032) adjacent valve galleries demineralizer resin ation 70-0 SRWS tank and transfer pump Spent resin and decant liquid 10, -015, -016, -022, -023, & 026) rooms ation 70-0 LRWS tank and transfer pump LRWS 08, -009, -011 through -014, -018 through -021, - rooms 24, & 025) ation 70-0 GRWS decay bed and Gaseous radioactive waste 037 & 038) condenser rooms ation 70-0 SRWS HIC filling room Spent resin and decant liquid 35) ation 70-0 SRWS HIC storage room Spent resin and decant liquid 34) ation 70-0 SRWS drum storage room Packaged solid radioactive

33) waste ation 70-0 LRWS processing equipment LRWS
05) room ation 70-0 LRWS drum dryer area LRWS 05) ation 100-0 Class A and low level solid Packaged solid radioactive
25) radwaste storage rooms waste ation 145-0 RWBVS equipment area RWBVS exhaust 02) 1: Figure 1.2-24 to Figure 1.2-26 depict room locations.

cale US460 SDAA 12.3-32 Revision 1

Scale Final Safety Analysis Report vation Room No. Room Name Radioactive North Wall East Wall South Wall West Wall Floor Ceiling ote 1) (Note 1) (Note 1) Source 0 006 Module 01 CVC ion CVC IXs, CVC 20 concrete 20 concrete 20 concrete 20 concrete Basemat 27.5 concrete exchanger valve room FLTs 0 007 Module 01 CVC ion CVC IXs, CVC 20 concrete 20 concrete 20 concrete 20 concrete Basemat 24 concrete exchanger enclosure FLTs 0 008 Module 01 CVC filter CVC IXs, CVC 20 concrete 20 concrete 20 concrete 48 concrete Basemat 24 concrete enclosure FLTs 0 009 Module 02 CVC ion CVC IXs, CVC 20 concrete 20 concrete 20 concrete 20 concrete Basemat 27.5 concrete exchanger valve room FLTs 0 010 Module 02 CVC ion CVC IXs, CVC 20 concrete 20 concrete 20 concrete 20 concrete Basemat 24 concrete exchanger enclosure FLTs 0 011 Module 02 CVC filter CVC IXs, CVC 20 concrete 20 concrete 20 concrete 20 concrete Basemat 24 concrete enclosure FLTs 0 012 Module 03 CVC ion CVC IXs, CVC 20 concrete 48 concrete 20 concrete 20 concrete Basemat 27.5 concrete exchanger valve room FLTs 0 013 Module 03 CVC ion CVC IXs, CVC 20 concrete 48 concrete 20 concrete 20 concrete Basemat 24 concrete exchanger enclosure FLTs 0 014 Module 03 CVC filter CVC IXs, CVC 20 concrete 20 concrete 20 concrete 20 concrete Basemat 24 concrete enclosure FLTs 0 024 Module 04 CVC ion CVC IXs, CVC 20 concrete 20 concrete 20 concrete 20 concrete Basemat 27.5 concrete exchanger valve room FLTs 0 025 Module 04 CVC ion CVC IXs, CVC 20 concrete 20 concrete 20 concrete 20 concrete Basemat 24 concrete exchanger enclosure FLTs 0 026 Module 04 CVC filter CVC IXs, CVC 20 concrete 48 concrete 20 concrete 20 concrete Basemat 24 concrete Radiation Protection Design Features enclosure FLTs 0 027 Module 05 CVC ion CVC IXs, CVC 20 concrete 20 concrete 20 concrete 20 concrete Basemat 27.5 concrete exchanger valve room FLTs 0 028 Module 05 CVC ion CVC IXs, CVC 20 concrete 20 concrete 20 concrete 20 concrete Basemat 24 concrete exchanger enclosure FLTs 0 029 Module 05 CVC filter CVC IXs, CVC 20 concrete 20 concrete 20 concrete 20 concrete Basemat 24 concrete enclosure FLTs 0 030 Module 06 CVC ion CVC IXs, CVC 20 concrete 20 concrete 20 concrete 48 concrete Basemat 27.5 concrete exchanger valve room FLTs 0 031 Module 06 CVC ion CVC IXs, CVC 20 concrete 20 concrete 20 concrete 48 concrete Basemat 24 concrete exchanger enclosure FLTs

Scale Final Safety Analysis Report vation Room No. Room Name Radioactive North Wall East Wall South Wall West Wall Floor Ceiling ote 1) (Note 1) (Note 1) Source 0 032 Module 06 CVC filter CVC IXs, CVC 20 concrete 20 concrete 20 concrete 20 concrete Basemat 24 concrete enclosure FLTs 0 034 LRW degasifier tank B LRW DGS B 48 concrete 32 concrete 32 concrete 32 concrete Basemat 32 concrete room 0 037 LRW degasifier tank A LRW DGS A 48 concrete 32 concrete 32 concrete 48 concrete Basemat 32 concrete room 0 040 Dry dock Pool water 48 concrete - 48 concrete 48 concrete Basemat -

0 to 041 Spent fuel pool Spent fuel 48 concrete - 48 concrete 48 concrete Basemat 36 concrete

-0 assemblies, Pool water 0 to 042 Reactor pool Pool water 48 concrete 48 concrete 48 concrete 48 concrete Basemat 30 concrete

-0 0 to - Module bays - Modules RXMs, Pool water 51.75 51.75 3.5 HDPE 51.75 Basemat 29 concrete

-0 01-03 concrete concrete panels, 5% concrete (TYP), 72 (TYP), 72 boron content concrete concrete (East (vertical (below EL 43-pool wall bioshield)

0) below EL 43-0) 0 to - Module bays - Modules RXMs, Pool water 3.5 HDPE 51.75 51.75 51.75 Basemat 29 concrete

-0 04-06 panels, 5% concrete concrete concrete boron content (TYP), 72 (TYP), 72 (vertical concrete (East concrete bioshield) pool wall (below EL 43-Radiation Protection Design Features below EL 43- 0) 0)

0 - Pipe chase - SRW resin SRW resin 24 concrete 24 concrete 24 concrete 48 concrete Basemat -

transfer line transfer line 0 109 Module 01 CVC CVC discharge 20 concrete 10 concrete 20 concrete 10 concrete 24 concrete 24 concrete recirculation pump valve line room 0 112 Module 02 CVC CVC discharge 20 concrete 10 concrete 20 concrete 10 concrete 24 concrete 24 concrete recirculation pump valve line room

Scale Final Safety Analysis Report vation Room No. Room Name Radioactive North Wall East Wall South Wall West Wall Floor Ceiling ote 1) (Note 1) (Note 1) Source 0 115 Module 03 CVC CVC discharge 20 concrete 10 concrete 20 concrete 10 concrete 24 concrete 24 concrete recirculation pump valve line room 0 123 Module 04 CVC CVC discharge 20 concrete 10 concrete 20 concrete 10 concrete 24 concrete 24 concrete recirculation pump valve line room 0 126 Module 05 CVC CVC discharge 20 concrete 10 concrete 20 concrete 10 concrete 24 concrete 24 concrete recirculation pump valve line room 0 129 Module 06 CVC CVC discharge 20 concrete 10 concrete 20 concrete 10 concrete 24 concrete 24 concrete recirculation pump valve line room 0 - Pipe chase - SRW resin SRW resin 24 concrete 24 concrete 24 concrete 48 concrete - -

transfer line transfer line 0 207 Modules 01-03 CVC HX CVC discharge 20 concrete 48 concrete 20 concrete 48 concrete 24 concrete 29 concrete valve gallery line, CVC HXs 0 208 Module 01 CVC HX room CVC discharge 20 concrete 20 concrete 48 concrete 48 concrete 24 concrete 24 concrete line, CVC HXs 0 209 Module 02 CVC HX room CVC discharge 20 concrete 20 concrete 48 concrete 20 concrete 24 concrete 24 concrete line, CVC HXs 0 210 Module 03 CVC HX room CVC discharge 20 concrete 48 concrete 48 concrete 20 concrete 24 concrete 24 concrete line, CVC HXs 0 213 MHS equipment room MHS HT 18 concrete 18 concrete 48 concrete 48 concrete 24 concrete 24 concrete 0 216 Modules 04-06 CVC HX CVC discharge 20 concrete 48 concrete 20 concrete 48 concrete 24 concrete 29 concrete Radiation Protection Design Features valve gallery line, CVC HXs 0 217 Module 04 CVC HX room CVC discharge 48 concrete 48 concrete 20 concrete 20 concrete 24 concrete 24 concrete line, CVC HXs 0 218 Module 05 CVC HX room CVC discharge 48 concrete 20 concrete 20 concrete 20 concrete 24 concrete 24 concrete line, CVC HXs 0 219 Module 06 CVC HX room CVC discharge 48 concrete 20 concrete 20 concrete 48 concrete 24 concrete 24 concrete line, CVC HXs 0 - Pipe chase - SRW resin SRW resin 24 concrete 24 concrete 24 concrete 48 concrete - -

transfer line transfer line 0 304 PCW equipment PCW HXs 48 concrete 48 concrete 48 concrete 48 concrete 24 concrete 24 concrete aisleway

Scale Final Safety Analysis Report vation Room No. Room Name Radioactive North Wall East Wall South Wall West Wall Floor Ceiling ote 1) (Note 1) (Note 1) Source 0 - Pipe chase - SRW resin SRW resin 24 concrete 24 concrete 24 concrete 48 concrete - 24 concrete transfer line transfer line 0 - Pipe chases - Modules CVC discharge 16 concrete 16 concrete 48 concrete 16 concrete - -

01-03 CVC discharge lines lines 0 - Pipe chases - Modules CVC discharge 48 concrete 16 concrete 16 concrete 16 concrete - -

04-06 CVC discharge lines lines 0 - Pipe chases - Modules CVC discharge 16 concrete 16 concrete 48 concrete 16 concrete - -

01-03 CVC discharge lines lines 0 - Pipe chases - Modules CVC discharge 48 concrete 16 concrete 16 concrete 16 concrete - -

04-06 CVC discharge lines lines

-0 - Pipe chases - Modules CVC discharge 16 concrete 16 concrete 48 concrete 16 concrete - 16 concrete 01-03 CVC discharge lines lines

-0 - Pipe chases - Modules CVC discharge 48 concrete 16 concrete 16 concrete 16 concrete - 16 concrete 04-06 CVC discharge lines lines 1: Figure 1.2-8 through Figure 1.2-18 depict room locations.

2: A 1" steel plate is placed above the entrance to the CVCS demineralizer valve gallery.

3: The vertical pipe chase enclosure containing the CVCS resin transfer line the to the SRWS extends from EL 25'-0" to EL 81'-0".

4: The reactor pool walls are typically 48" concrete, with the exception of areas immediately north, south, and east of the operating RXMs, which are described Radiation Protection Design Features Module bays" with thier own entry in the table.

5: The vertical pipe chase enclosures containing the CVCS discharge lines from the RXMs to the CVC heat exchangers extend from EL 70'-0" to EL 111'- 7".

Scale Final Safety Analysis Report oom Source Term North Wall East Wall South Wall West Wall Floor Ceiling Labryinth Walls mber te 1) 05 LRW Processing Exterior Exterior 24 Concrete 24 Concrete Facility Basemat 24 Concrete - 24 Concrete Equipment subgrade wall subgrade wall (Entrance)

- 24 Concrete (Drum dryer Area)

- 24 Concrete (Drum dryer Accumulator Tank Area)

- 24 Concrete (Ion Exchanger area)

- 24 Concrete (Charcoal Filter Area) 08 LRW LCW Sample 24 Concrete 24 Concrete 24 Concrete 24 Concrete Facility Basemat 24 Concrete - 24 Concrete (Doorway)

Tank Pumps - 12 Concrete (Pump Divider) 09 LRW HCW Sample 24 Concrete 24 Concrete 24 Concrete 24 Concrete Facility Basemat 24 Concrete - 24 Concrete (Doorway)

Tank Pumps - 12 Concrete (Pump Divider) 10 SRW PST Pumps 24 Concrete 36 Concrete 36 Concrete 24 Concrete Facility Basemat 24 Concrete - 24 Concrete (Doorway)

- 12 Concrete (Pump Divider) 24 LRW LCW Collection 24 Concrete 24 Concrete 24 Concrete 24 Concrete Facility Basemat 24 Concrete - 24 Concrete (Doorway)

Tank Pumps - 12 Concrete (Pump Divider) 25 LRW HCW Collection 24 Concrete 24 Concrete 24 Concrete 24 Concrete Facility Basemat 24 Concrete - 24 Concrete (Doorway)

Tank Pumps - 12 Concrete (Pump Divider) 26 SRW SRST Pumps 36 Concrete 36 Concrete 24 Concrete 24 Concrete Facility Basemat 24 Concrete - 24 Concrete (Doorway)

- 12 Concrete (Pump Divider)

Radiation Protection Design Features 11 LRW LCW Sample 24 Concrete 24 Concrete 24 Concrete 24 Concrete Facility Basemat 24 Concrete N/A Tank 12 LRW LCW Sample 24 Concrete 24 Concrete 24 Concrete 24 Concrete Facility Basemat 24 Concrete N/A Tank 18 LRW LCW Collection 24 Concrete 24 Concrete 24 Concrete 24 Concrete Facility Basemat 24 Concrete N/A Tank 19 LRW LCW Collection 24 Concrete 24 Concrete 24 Concrete 24 Concrete Facility Basemat 24 Concrete N/A Tank 13 LRW HCW Sample 24 Concrete 24 Concrete 24 Concrete 24 Concrete Facility Basemat 24 Concrete N/A Tank

Scale Final Safety Analysis Report oom Source Term North Wall East Wall South Wall West Wall Floor Ceiling Labryinth Walls mber te 1) 14 LRW HCW Sample 24 Concrete 36 Concrete 24 Concrete 24 Concrete Facility Basemat 24 Concrete N/A Tank 20 LRW HCW Collection 24 Concrete 24 Concrete 24 Concrete 24 Concrete Facility Basemat 24 Concrete N/A Tank 21 LRW HCW Collection 24 Concrete 36 Concrete 24 Concrete 24 Concrete Facility Basemat 24 Concrete N/A Tank 15 SRW PST 36 Concrete 36 Concrete 36 Concrete 36 Concrete Facility Basemat 36 Concrete N/A 16 SRW PST 36 Concrete 36 Concrete 36 Concrete 36 Concrete Facility Basemat 36 Concrete N/A 22 SRW SRST 36 Concrete 36 Concrete 36 Concrete 36 Concrete Facility Basemat 36 Concrete N/A 23 SRW SRST 36 Concrete 36 Concrete 36 Concrete 36 Concrete Facility Basemat 36 Concrete N/A 17 Pipe Chase 24 Concrete 24 Concrete 24 Concrete 24 Concrete Facility Basemat 24 Concrete N/A 29 PCU FLT 30 Concrete Exterior Exterior 30 Concrete Facility Basemat 30 Concrete N/A subgrade wall subgrade wall 30 PCU FLT 30 Concrete 30 Concrete Exterior 30 Concrete Facility Basemat 30 Concrete N/A subgrade wall 32 PCU IX 24 Concrete 30 Concrete Exterior 24 Concrete Facility Basemat 24 Concrete N/A subgrade wall 33 SRW Drum Storage 36 Concrete 36 Concrete 24 Concrete Exterior Facility Basemat 24 Concrete 20 Concrete subgrade wall 34 SRW HIC Storage 36 Concrete 36 Concrete 36 Concrete Exterior Facility Basemat 36 Concrete N/A subgrade wall 35 SRW HIC Filling 36 Concrete 36 Concrete 36 Concrete Exterior Facility Basemat 36 Concrete N/A Radiation Protection Design Features subgrade wall 37 GRW Vapor 24 Concrete 36 Concrete 24 Concrete Exterior Facility Basemat 24 Concrete N/A Condensers / Gas subgrade wall Coolers 38 GRW Charcoal Beds 24 Concrete 24 Concrete 24 Concrete Exterior Facility Basemat 24 Concrete 24 Concrete subgrade wall 1: Refer to Figure 1.2-22 through Figure 1.2-24 for room locations.

2. The equivalent attenuation to an additional 4.5 inches of lead is provided for a HIC process shield.

3: The equivalent attenuation to an additional one inch of steel in addition to the LRWS process skid.

4: A penetration to the HIC storage room is modeled with a 1ft concrete shadow shield.

dioactive Waste Radioactive Waste Radioactive Waste Building Room Door Shielding uilding Door # Building Room # Description (Note 2)

(Note 1) 034A 034 SRWS HIC storage room 75% equivalent wall 035A 035 SRWS HIC filling room 20% equivalent wall 015A 015 SRWS PST A room 45% equivalent wall 016A 016 SRWS PST B room 45% equivalent wall 022A 022 SRWS SRST A room 100% equivalent wall 023A 023 SRWS SRST B room 100% equivalent wall 030A 030 PCWS filter A room 60% equivalent wall 029A 029 PCWS filter B room 60% equivalent wall 1: Figure 1.2-22, Figure 1.2-23 and Figure 1.2-24 depict room locations.

2: Door shielding is given as a percentage of the effective shielding provided by the barrier in which the door is located.

cale US460 SDAA 12.3-39 Revision 1

Scale Final Safety Analysis Report Area Monitor Estimated Dynamic Principal Basis for Dynamic Range PAM Variable Detection Range Parameter Type measured der bioshield monitors Fixed area 1E+0 to 1E+7 rem/hr gamma RG 1.97, Rev. 5 Type B, Type C Equipment Qualification Post-Accident and Type F Radiological Source Term Hot lab Fixed area 1E-1 to 1E+4 mrem/hr gamma RG 1.97, Rev. 5 Type E ANSI/ANS-HPSSC-6.8.1-1981 Hot lab Fixed airborne 3E-10 to 1E-6 µCi /cc Cs-137: RG 1.97, Rev. 5 Type E Radiological Source Term fety instrument rooms Fixed area 1E-1 to 1E+4 rem/hr gamma RG 1.97, Rev. 5 Type E ANSI/ANS-HPSSC-6.8.1-1981 AS switchgear rooms Fixed area 1E-1 to 1E+4 mrem/hr gamma RG 1.97, Rev. 5 Type E ANSI/ANS-HPSSC-6.8.1-1981 CR envelope - main Fixed area 1E-1 to 1E+4 mrem/hr gamma RG 1.97, Rev. 5 Type E control room ARM ANSI/ANS-HPSSC-6.8.1-1981 CR envelope - MCR Fixed airborne 1E-7 to 1E-1 µCi/cc Kr-85, Xe-133: RG 1.97, Rev. 5 Type E area 1E-10 to 1E-6 µCi/cc Cs-137: , ANSI/HPS 13.1-2011 orne radiation monitor 1E-10 to 1E-5 µCi/cc I-131:

chnical support center Fixed area 1E-1 to 1E+4 mrem/hr gamma RG 1.97, Rev. 5 Type E ANSI/ANS-HPSSC-6.8.1-1981 Primary Sampling Fixed Area 1E-1 to 1E+4 mrem/hr gamma RG 1.97, Rev. 5 Type E Equipment ANSI/ANS-HPSSC-6.8.1-1981 ontainment Sampling Fixed Area 1E-1 to 1E+4 mrem/hr gamma RG 1.97, Rev. 5 Type E System Equipment ANSI/ANS-HPSSC-6.8.1-1981 Refuel Pool Area Fixed airborne 3E-7 to 1E+4 µCi/cc Kr-85, Xe-133: Regulatory Guide 1.97, Rev. 5 Type E Radiation Protection Design Features ontinuous Airborne 5E-12 to 1E+2 µCi/cc Cs-137: , Radiological Source Term Monitor 4E-12 to 1E+2 µCi/cc I-131: ANSI 42.18-2004 Refuel Pool Area Fixed Area 1E-4 to 1E+4 mrem/hr gamma ANSI/ANS-HPSSC-6.8.1-1981 Type E orth Steam Gallery Fixed Airborne 3E-7 to 1E+4 µCi/cc Kr-85, Xe-133: Regulatory Guide 1.97, Rev. 5 Type E ontinuous Airborne 5E-12 to 1E+2 µCi/cc Cs-137: , Radiological Source Term Monitor 4E-12 to 1E+2 µCi/cc I-131: ANSI 42.18-2004 outh Steam Gallery Fixed Airborne 3E-7 to 1E+4 µCi/cc Kr-85, Xe-133: Regulatory Guide 1.97, Rev. 5 Type E ontinuous Airborne 5E-12 to 1E+2 µCi/cc Cs-137: , Radiological Source Term Monitor 4E-12 to 1E+2 µCi/cc I-131: ANSI 42.18-2004

Scale Final Safety Analysis Report Building and Area Detector Quantity / Principal Parameter Measured Nominal Range PAM / Type Elevation Type eactor Building Degasifier room A 1 / Noble gas Kr-85, Xe-133: 3E-4 to 1E+3 µCi / cc No elevation 25 Degasifier room B 1 / Noble gas Kr-85, Xe-133: 3E-4 to 1E+3 µCi / cc No eactor Building Hot lab 1 / Particulate Cs-137: 3E-10 to 1E-6 µCi /cc Yes / E elevation 85 eactor Building Refuel Pool 1 / Noble gas Kr-85, Xe-133: 3E-7 to 1E+4 µCi / cc Yes / E evation 100'-0" North Steam Gallery 1 / Particulate Cs-137: , 5E-12 to 1E+2 µCi / cc South Steam Gallery 1 / Iodine I-131: 4E-12 to 1E+2 µCi / cc dioactive Waste Hot shop 1 / Particulate Cs-137: 3E-10 to 1E-6 µCi /cc No elevation 100 dioactive Waste Gaseous radioactive waste 1 / Noble gas Kr-85, Xe-133: 3E-7 to 1E-2 µCi /cc No ding elevation 70 process tank area 1 / Particulate Cs-137: 3E-10 to 1E-6 µCi /cc 1 / Iodine I-131: 3E-10 to 5E-8 µCi /cc ontrol Building Main Control Room 1/Noble Gas Kr-85, Xe-133: 1E-7 to 1E-1 µCi/cc Yes / E elevation 125 1/Particulate Cs-137: , 1E-10 to 1E-6 µCi/cc 1/Iodine 1E-10 to 1E-5 µCi/cc I-131:

Radiation Protection Design Features

Scale Final Safety Analysis Report Building and Area Detector Quantity / Type Principal Parameter Nominal Range PAM / Type Elevation Measured eactor Building CVCS filters 6 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No elevation 25 RWDS sump pump areas 4 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No eactor Building CVCS recirculation rooms 2 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No elevation 40 eactor Building PCWS equipment 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No elevation 55 CVCS recirculation pumps 2 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No MHS heater room 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No eactor Building PSS sample panel 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr Yes / E elevation 70 PCWS heat exchanger 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No Safety I&C and EDAS equipment 2 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr Yes / E rooms eactor Building Refuel Bridge 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No elevation 85 Refuel Pool 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr Yes / E Safety I&C and EDAS equipment 2 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr Yes / E rooms Hot Lab 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr Yes / E eactor Building North PSS sample panel 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr Yes / E levation 100 South PSS sample panel 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr Yes / E Inside bioshield monitor 12 / gamma-sensitive gamma 1E0 to 1E+7 rem/hr Yes / B & C & F eactor Building Module Maintenance Center 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No Radiation Protection Design Features levation 126 North Equipment 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No South Equipment 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No eactor Building North RBVS AHU 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No levation 146' South RBVS AHU 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No ontrol Building Main CRE 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr Yes / E levation 125' Technical support center 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr Yes / E

Scale Final Safety Analysis Report Building and Area Detector Quantity / Type Principal Parameter Nominal Range PAM / Type Elevation Measured dioactive Waste LRWS equipment area 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No ilding elevation Reactor Building Access 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No 70 RWDS sump pumps 4 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No LRWS storage tank pump rooms 4 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No SRWS storage tank pump rooms 2 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No SRWS HIC storage room 1 / gamma-sensitive gamma 1E-1 to 1E+4 rem/hr No PCWS filter room 2 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No Waste drum storage room 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No dioactive Waste Self-propelled mobile transporter 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No ilding elevation (SPMT) 100 Class A Waste Storage Room 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No Waste management control room 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No Hot Shop area 1 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No urbine Building General area 2 / gamma-sensitive gamma 1E-1 to 1E+4 mrem/hr No levation 100 dioactive Waste RBV Filter Area 1 / gamma sensitive gamma 1E-1 to 1E+4 mrem/hr No ilding Elevation 119' Radiation Protection Design Features

Regulatory Guide 4.21 Evaluation stem System Name System System Name ode Code auxiliary boiler system PCWS pool cooling and cleanup system S air cooled condenser system PLDS pool leakage detection system S balance-of-plant drain system PSS process sampling system containment evacuation system RBVS Reactor Building HVAC system S containment flooding and drain system RCCWS reactor component cooling water system WS chilled water system RCS reactor coolant system condensate polisher resin regeneration RWBVS Radioactive Waste Building HVAC system system S normal control room HVAC system RWB Radioactive Waste Building S chemical and volume control system RWDS radioactive waste drain system S decay heat removal system RXB Reactor Building S demineralized water system SCWS site cooling water system S condensate and feedwater system SRWS solid radioactive waste system WS gaseous radioactive waste system UHS ultimate heat sink S liquid radioactive waste system UWS utility water system main steam system cale US460 SDAA 12.3-44 Revision 1

Objective Design Features ctive 1- Minimize the The ABS uses proven, corrosion resistant material for the system components in ntial for leaks or spills and accordance with industry codes and standards. This design feature also applies to ide containment areas Objective 3.

The ABS distribution piping uses welded pipe construction as much as practicable.

This design feature minimizes the potential for contamination to spread. This design feature also applies to Objectives 3 and 4.

The valves are rated specifically for the required ABS pressure and temperature with hard face seats used for sealing to minimize leakage.

ctive 2- Provide leak The ABS is provided with several pressure, level, and flow instruments throughout the ction capability system to monitor system performance.

The ABS steam header is designed such that only one module can supply steam to the header at any given moment.

The ABS has radiation monitoring on vents and drains. If radiation is detected, steam supply valves are shut and an alarm alerts operations staff.

ctive 3- Reduce The ABS is designed to preclude contamination of connecting systems.

amination to minimize Isolation valves are used to minimize the possibility of cross contamination among ases, cross-contamination multiple NPMs in the event of a SG tube leak.

waste generation ctive 4- Facilitate Parts of the ABS are designed using modular vendor skids, which facilitates ommissioning decommissioning.

ctive 5- Operating COL item rams and documentation ctive 6- Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-45 Revision 1

Objective Design Features ctive 1 - Minimize the The air cooled condenser system (ACCS) is designed to minimize the effects of ntial for leaks or spills and corrosion using a combination of corrosion resistant materials.

ide containment areas Provisions for representative grab sampling are provided in the gaseous discharge line and allow for removal and return of the sample as part of an integrated skid system. The sample connections include a supply and return connection to facilitate purging after a sample is taken. This feature also prevents operator contact with radioactive material and minimizes contamination as the sample is returned to the process line. The sample is returned directly to the process line to minimize contamination.

ctive 2 - Provide leak The ACCS condenser air removal system (CARS) has radiation monitors that meet ction capability the requirements of a continuous radiation monitor per the EPRI primary to secondary leakage guidelines. Manual sampling points are available in the event the radiation monitors are inoperable.

ctive 3 - Reduce Steam generated in the SGs is not radioactive during regular operating conditions. In amination to minimize the unlikely event of a primary to secondary system leak due to steam generator tube ases, cross-contamination failure, the MSS and the FWS provide for closure of isolation valves to minimize the waste generation propagation of contamination into the CARS.

Radiation monitors have two setpoints to minimize release of contamination to the environment.

ctive 4 - Facilitate The ACCS has removable/maintainable/replaceable outside of radiation field and not ommissioning expected to have contamination for regular operation ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-46 Revision 1

Objective Design Features ctive 1- Minimize the The BPDS uses proven materials in accordance with ASME B31.1. This design ntial for leaks or spills and feature reduces the potential for leaks.

ide containment areas The wastewater and chemical waste collection tanks are enclosed in stainless-steel-lined concrete containments to serve as two boundaries against leakage to the environment. This design feature also applies to Objective 3.

The BPDS contains above ground and below ground SSC. Outdoor SSC located above ground are provided with freeze protection insulation and drains to prevent rupture from freezing.

The BPDS has high-level alarms on the wastewater and chemical waste collection tanks that indicate overflow.

ctive 2 - Provide leak The wastewater and chemical waste collection tanks are provided with leak detection ction capability capabilities. Radiation monitors are located on drain lines with the potential to be contaminated.

The BPDS has alarms associated with level, pressure, radiation, and leak detection.

ctive 3 - Reduce The BPDS piping and component materials are designed for the 60-year design life of amination to minimize the plant.

ases, cross-contamination Drain lines in the BPDS are sloped, which reduces accumulation of solid forms of waste generation radioactivity within the piping.

Floor drains and pump suctions are provided with maintainable strainers to promote system cleanliness and longevity.

ctive 4 - Facilitate The BPDS collects and segregates normally non-radioactive liquid waste from areas ommissioning associated with power-related or process-related outside the RCA. Being outside the RCA allows access to facilitate decommissioning.

ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-47 Revision 1

System Objective Design Features ctive 1 - Minimize the The CES uses welded components and welded piping to the extent practicable to ntial for leaks or spills and minimize potential for leaks and spills.

ide containment areas Stainless steel is the material for wetted components, including the sample vessel, condenser, and valves, to provide corrosion resistances and to minimize degradation and particulate generation. This design feature also applies to Objective 3.

The CES equipment vents and drains are routed in closed lines to the RWDS. This design feature also applies to Objective 3.

ctive 2 - Provide leak The gaseous discharge path has radiation monitors for monitoring leaks.

ction capability The CES control system uses input from pressure, temperature, sample vessel level, valve position, and radiation instruments to monitor system performances and control vacuum pump speed. The instrumentation on the CES sample vessel provides indication that the system may have developed a leak.

ctive 3 - Reduces The CES sample vessel has provisions for flushing with demineralized water and for amination to minimize purging with nitrogen.

ases, cross-contamination waste generation ctive 4 - Facilitate Most CES components are specified for the 60-year design life of the plant. The filters ommissioning are specified for a 10-year life with planned replacement. This design feature also applies to Objective 3.

The CES components outside of the CNV are in shielded equipment galleries separate from SSC that are expected to generate high radiation levels. This feature reduces equipment contamination and reduces the effort for decommissioning the CES components.

ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-48 Revision 1

Drain System Objective Design Features ctive 1 - Minimize the CFDS vents and drains are sent to the RWDS via closed piping. Pump leakage and ntial for leaks or spills and leakage from the containment drain separator tank is collected by the RWDS. This ide containment areas design feature also applies to Objective 3.

The CFDS piping is designed using proven materials in accordance with ASME B31.1. This design feature reduces the potential for leaks.

The CFDS piping and wetted components are designed using corrosion-resistant materials that reduce the potential for leaks and contamination.

ctive 2 - Provide leak Pressure, flow, temperature, and level transmitters provided throughout the system ction capability monitor system performance and possible system pressure boundary failure.

ctive 3 - Reduce A HEPA filter is installed in the containment drain separator tank vent line to capture amination to minimize radioactive particles before discharging the air to the RBVS.

ases, cross-contamination High radioactivity measured by the CFDS process radiation monitor results in waste generation automatic isolation of the line on a high-radioactivity indication. This filtration and automatic function minimizes transfer of radioactive effluent to the RXB exhaust stack.

ctive 4 - Facilitate Embedded piping is minimized. This design prevents ground contamination and ommissioning reduces decontamination effort during the decommissioning.

ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-49 Revision 1

Objective Design Features ctive 1 - Minimize the The CHWS uses proven materials that are corrosion-resistant materials for piping and ntial for leaks or spills and components, like stainless steel, for piping (designed according to ASME B31.1).

ide containment areas The CHWS water is a glycol solution to prevent freezing in the HVAC coils during the winter months.

ctive 2 - Provide leak The CHWS has localized pressure monitoring at the interface with the GRWS and ction capability LRWS. Changes in pressure can indicate a leak.

The chillers include factory-installed microprocessor control systems to monitor and control chiller functions.

ctive 3 - Reduce The CHWS is maintained at a higher pressure than the GRWS and the LRWS at the amination to minimize heat exchanger. The CHWS is isolated to and from the LRWS skid if the pressure ases, cross-contamination difference is less than the setpoint to avoid the possibility of the CHWS being at a waste generation lower pressure than LRWS.

ctive 4 - Facilitate The CHWS components are designed with elements that can be easily removed ommissioning during decommissioning.

ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-50 Revision 1

Regeneration System Objective Design Features ctive 1 - Minimize the The CPS materials are selected based on compatibility to temperature, pressure, and ntial for leaks or spills and chemistry of the various resins, demineralized water, sulfuric acid, and sodium ide containment areas hydroxide. Piping and non-replaceable component materials are consistent with the 60-year design life. CPS piping is designed to ASME B31.1. This material selection and design process reduces the likelihood of equipment failures and leaks. This design feature also applies to Objectives 3 and 4.

Adequate workspace and laydown areas are provided to perform maintenance on equipment and other CPS components. Adequate space allows for preventative maintenance to reduce leaks. This also applies to Objectives 3 and 4.

ctive 2 - Provide leak The CPS is has radiation monitors to alert personnel of changing radiological ction capability conditions, and to alert the MCR of previously undetected primary to secondary leakage manifesting during resin transfer.

ctive 3 - Reduce The BPDS supports the CPS by accepting drains and neutralized water from the amination to minimize neutralization water pump. This feature minimizes the spread of contamination if the ases, cross-contamination CPS becomes contaminated.

waste generation The resin in the cation regeneration vessel is washed and recycled back to the CPS.

This feature minimizes waste resin generation.

ctive 4 - Facilitate The CPS is located above ground in the Turbine Generator Building (TGB), in the ommissioning yard near the TGB and the offsite chemical storage area. The above ground placement of many components facilitates decommissioning.

The CPS structures, systems, and components are not located in buildings or areas considered a radiation hazard, which facilitates decommissioning.

ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-51 Revision 1

Ventilation System Objective Design Features ctive 1 - Minimize the The CRVS air handling units provide conditioned air to maintain the control rooms ntial for leaks or spills and environment within an acceptable range. If the outside air becomes radioactively ide containment areas contaminated, the outside air is filtered. This feature minimizes the potential for contaminated air from entering the system. This design feature also applies to Objective 3.

The CRVS components are designed in accordance with applicable industry codes and standards.

The CRVS ductwork is designed to various leakage classes per ASME AG-1. This feature limits the allowable leakage from the system.

Drains from the potentially contaminated CRVS filter unit are routed to the BPDS. This design feature also applies to Objective 3.

ctive 2 - Provide leak The CRVS has radiation monitors both upstream and downstream of the filter unit.

ction capability ctive 3 - Reduce The CRVS maintains the CRB at a positive ambient pressure relative to the RXB and amination to minimize the outside atmosphere to control the ingress of potentially airborne radioactivity.

ases, cross-contamination The CRVS filter unit filters the outside make-up air when radiation is detected in the waste generation outside air intake ductwork.

Upon detection of a high radiation level in the outside air intake, the system is realigned so that 100 percent of the outside air passes through the CRVS filter unit, containing HEPA and charcoal filters, to filter outside air and minimize radiation exposure to personnel within the CRB.

ctive 4 - Facilitate Most of the CRVS is above ground. This design feature facilitates decommissioning.

ommissioning ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-52 Revision 1

System Objective Design Features ctive 1 - Minimize the The CVCS tanks, piping, and valves are designed to the applicable ASME code with ntial for leaks or spills and corrosion resistant materials to minimize degradation and particulate generation over ide containment areas the 60-year design life of the plant. Welded construction minimizes the potential for leaks as practicable.

A chemical mixing allows the addition of chemicals into the primary coolant system to minimize the potential for primary water stress-corrosion cracking and resultant equipment failures.

The discharge lines from pressure relief valves are routed to the RWDS.

The floor and equipment drains are provided for CVCS and MHS equipment to direct spills or leaks to the nearest drain hub or sump in the RWDS by gravity.

The floor in each equipment room is sloped to facilitate the collection of leaks and spills.

ctive 2 - Provide leak The CVCS ion exchange vessels, filters, and resin traps are in cubicles equipped with ction capability moisture sensors for early leak detection. The CVCS heat exchangers and pumps drain to a RWDS sump.

The CVCS expansion tank has a level transmitter that monitors the water level in the tank to provide indication of CVCS leakage.

The CVCS provides the capability to inject argon into the RCS, increasing the sensitivity of SG tube leak detection.

The CVCS includes flow, temperature, and pressure indications throughout the system to monitor system performance, including mass flow rate in the CVCS makeup line, the letdown line to the LRWS, and the NPM injection and discharge lines. The mass flow mismatch warns operators of abnormal conditions.

The ARMs near the components assist in detecting potential airborne leaks.

Most indicators have remote capabilities to ensure prompt alerting of operators.

ctive 3 - Reduce A continuous sample connection is provided on the CVCS module discharge line to amination to minimize the PSS, which is also returned to the CVCS to reduce waste generation.

ases, cross-contamination Utility connections are designed with a minimum of two barriers to prevent cross waste generation contamination of non-radioactive systems from potentially radioactive systems. For example, DWS and the boron addition system are aligned to independent CVCS pumps for boration and dilution with dual containment isolation valves for each CVCS containment penetration. There are double isolation valves upstream and downstream of each CVCS recirculation pump, ion exchanger, resin trap and filter.

An automatic feature diverts flow around the ion exchangers if the fluid temperature exceeds the high temperature set point for ion exchanger resin protection, preventing resin damage and minimizing waste generation.

The ion exchange and reactor coolant filters remove particulate and impurities from the CVCS water. This feature reduces the contamination of downstream equipment.

ctive 4 - Facilitate The CVCS components are designed for the 60-year design life of the plant.

ommissioning ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-53 Revision 1

Objective Design Features ctive 1 - Minimize the The decay heat removal system (DHRS) piping and components are designed to ntial for leaks or spills and ASME standards, and use welded construction and corrosion resistant materials. This ide containment areas feature also applies to Objective 3.

ctive 2 - Provide leak The DHRS is provided with temperature indications, calculated water level in the SG, ction capability and steam and feed water flow mass differences to indicate system performance and identify system leaks.

ctive 3 - Reduce A portion of the DHRS is located above the reactor pool water level under the amination to minimize bioshield, with the remaining portion of the system located under water in the reactor ases, cross-contamination pool. This arrangement reduces the potential for spreading contaminated steam or waste generation fluid into the RXB atmosphere.

ctive 4 - Facilitate The DHRS is designed for the 60-year design life of the plant and is designed, to the mmissioning extent practicable, for removal.

ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-54 Revision 1

Objective Design Features ctive 1 - Minimize the The DWS tanks and piping system are designed and fabricated according to industry ntial for leaks/ spills and codes and standards. This feature minimizes the potential for leaks. This feature also ide containment areas applies to Objective 3.

The DWS uses stainless steel piping, valves, and tanks to reduce the potential that corrosion results in leaks. This feature also applies to Objective 3.

ctive 2 - Provide leak The DWS incorporates radiation monitors to detect the backflow of contamination into ction capability the DWS.

ctive 3 - Reduce The DWS contains no radioactive substances but does interface with radioactive amination to minimize systems. User distribution lines are equipped with backflow preventers to prevent ases, cross-contamination contamination of the DWS. Isolation valves allow for system isolation in the event of a aste generation line break or other abnormal condition.

ctive 4 - Facilitate The DWS components are designed for 60-year design life with elements like ommissioning aboveground piping that can be easily removed during decommissioning.

ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-55 Revision 1

System Objective Design Features ctive 1 - Minimize the The FWS piping and components are designed to appropriate industry codes and ntial for leaks/ spills and standards, and are, where appropriate, made of corrosion resistant material that is ide containment areas compatible with the operating environment of FWS. This design feature reduces the potential for leaks.

The FWS includes nonsafety-related valves downstream of some safety-related valves. These redundant valves reduce the potential for leaks.

ctive 2 - Provide leak Grab sampling locations are provided in several locations to monitor the chemical ction capability composition and radiation contamination level of the FWS.

ctive 3 - Reduce The FWS includes a condensate polisher skid that treat and clean the feedwater to amination to minimize remove corrosion products and ionic impurities. A condensate strainer is located ases, cross-contamination upstream of each condensate pump to filter out foreign materials. These design aste generation features can reduce cross-contamination.

The FWS drains to the BPDS. This also applies to Objective 2.

ctive 4 - Facilitate The FWS piping is routed above the ground, as much as practicable. This routing ommissioning facilitates the decommissioning effort.

Many FWS components are located outside the RCA, making them easier to decontaminate and decommission.

ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-56 Revision 1

System Objective Design Features ctive 1 - Minimize the The GRWS uses low leakage valves (e.g., packless metal diaphragm valves) ntial for leaks or spills and wherever possible.

ide containment areas Embedded piping is minimized, and liquid containing lines are sloped to facilitate drainage (also meets Objective 4 of RG 4.21).

The GRWS components are designed using welded construction to minimize leaks.

In-line radiation monitors minimize contamination by returning samples to the process stream and do not require interfaces with non-contaminated systems for purging (also meets Objective 3 of RG 4.21).

ctive 2 - Provide leak Radiation monitors are provided near system components and cubicles to detect ction capability leakage from the GRWS.

Gas analyzers detect potentially explosive gas mixtures to enable operators to prevent an event that challenges system boundary integrity.

ctive 3 - Reduce The GRWS component materials are selected for reliable service for the 60-year amination to minimize design life, reducing waste generation from replacing components.

ases, cross-contamination Components are designed for reliability using industry codes and standards, per RG waste generation 1.143, minimizing the potential for cross-contamination and releases.

Welding techniques and material finishes are designed to provide smooth internal surfaces for decontamination. This design also meets Objective 1 and 4.

The GRWS gas sampler return samples to the process stream while also containing provisions to take a grab sample.

The GRWS piping arrangement is routed to reduce the total length of piping.

ctive 4 - Facilitate The GRWS components are designed for 60-year design life and easily removable ommissioning elements during decommissioning Nitrogen is provided to purge and decontaminate the system internals before disassembly (also meets Objective 3 of RG 4.21).

ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-57 Revision 1

System Objective Design Features ctive 1 - Minimize the The LRWS components, which include collection and sample tanks, are made of ntial for leaks or spills and stainless steel material and are of welded construction to minimize the potential for ide containments areas leakage and unintended contamination of the facility and the environment. This design feature also applies to Objectives 3 and 4.

The LRWS tanks are designed with sufficient capacity to provide liquid waste storage during normal operation, including anticipated operational occurrences. Redundant collection and sample tanks are provided to minimize the interruption of normal processing operation.

The LRWS is designed without embedded piping and a minimum of buried piping.

Buried LRWS piping or influent streams to the LRWS that are from outside of buildings is double walled with leak detection. Pipe leakage is either directed back to RWDS sumps or prevented by a pressure differential, that provides two barriers and thus prevents the spread of contaminations. This design feature also applies to Objective 3.

ctive 2 - Provide leak LRWS tanks are designed with level indicating transmitters, protected by isolated ction capability diaphragms, to provide safe operation of the SSC. The instruments provide alarms to the MCR and the waste management control room (WMCR) to alert operators to take appropriate action upon high liquid tank level.

The LRWS tank cubicles are provided with leak detection instrumentation to alarm for operator actions if leakage occurs. The LRWS leak detection is designed to detect small leakage quantities, which facilitates early detection.

Radiation monitors are provided in the LRWS processing area to detect airborne activity from leaks.

Pump bed plates that drain to the nearest floor drain are provided for LRWS transfer pumps to collect pump leakages.

ctive 3 - Reduce The SSC are designed with life-cycle planning through the use of materials amination to minimize compatible with the chemical, physical, and radiological environment in the nuclear ases, cross-contamination industry, thus minimizing waste generation.

waste generation The floor drains, equipment drains, and chemical drains are collected and segregated in the HCW and LCW tanks accordingly. The LRWS is a batch operation process; therefore, treatment of HCW and LCW type wastes are determined through sampling and analyses, then the wastes are routed to appropriate treatment processes that minimize cross-contamination and potential mixed waste generation.

The LRWS process piping containing contaminated solids are sized with sufficient velocities and sloped as necessary to facilitate flow and prevent the settling of solids.

Where interfaces exist with utilities, such as compressed air and gas and service water, double isolation is provide to prevent cross contamination of clean systems by LRW.

Connections to the demineralized water break tank are provided to flush and clean LRWS tanks to facilitate maintenance, inspection and removal of radioactive components.

The clean-in-place skid is provided to flush and clean the reverse osmosis skid to facilitate maintenance ctive 4 - Facilitate The LRWS is comprised of skid packages to facilitate eventual removal and ommissioning decommissioning. The SSC are designed for a 60-year dessign life of plant.

The LRWS is designed to aid decontamination and decommissioning activities.

Design features, such as material type, welding techniques, surface finishes, and equipment placement, are incorporated into the design to facilitate ALARA and minimize decontamination and minimize waste generation cale US460 SDAA 12.3-58 Revision 1

Objective Design Features ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-59 Revision 1

Objective Design Features ctive 1 - Minimize the The MSS piping is made of corrosion-resistant materials and designed in accordance ntial for leaks or spills and with ASME code. The fluid chemistry is maintained to reduce corrosion and minimize ide containment areas the potential for system leaks. This design feature also applies to Objective 3.

ctive 2 - Provide leak The steam line radiation monitors are designed to detect SG tube leaks.

ction capability Sampling capability is provided for the MSS to analyze the chemical composition.

Radiation monitors in the RBVS and ARMs can assist in detecting steam leaks into the RXB.

The air-cooled condenser system radiation monitors are designed to monitor effluents coming from the CARS and are designed to detect SG tube leaks.

ctive 3 - Reduce Fluid leaks from the MSS in the RXB and the TGB are collected by the RWDS and amination to minimize BPDS, respectively.

ases, cross-contamination The CPS is provided to cleanup the secondary coolant to reduce the level of waste generation radionuclide contamination and minimize releases, cross-contamination, and waste generation.

ctive 4 - Facilitate The MSS components are designed for the 60-year design life of the plant and are ommissioning designed, to the extent practicable, as discreet assemblies to facilitate decommissioning. The piping and equipment are above ground, as much as practicable.

The MSS piping has smooth surfaces to facilitate decommissioning.

ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-60 Revision 1

System Objective Design Features ctive 1 - Minimize the Leakage is captured to prevent system leaks, and drainage of the system is collected ntial for leaks or spills and and processed for radioactive waste cleanup. This design feature also applies to ide containment areas Objective 3.

The PCWS uses proven, corrosion-resistant materials for piping and components, like stainless steel, for piping (designed according to ASME B31.1), valves, pumps, filter housings, demineralizers, and wetted parts of the heat exchangers.

The PCWS filters and demineralizers, with their resin traps, are segregated and individually shielded, and resin transfer lines are routed through shielded chases.

Drainage from the PCWS filters is sent to the RWDS for collection before being sent to the LRWS for further processing.

Major system equipment is supplied with drains that connect to the RWDS that enables the equipment to be drained to sumps while keeping contaminated water within system piping to help maintain contamination control during maintenance.

The PCWS surge control tank is designed with a catch basin to contain the total volume the tank plus freeboard. The catch basin contains the leakage and transfers the fluid to the LRWS collection tanks. Using stainless steel components and piping reduces corrosion and the potential for leaks.

The pool water from a surge event is processed through the PCWS and stored in the PCWS surge control storage tank instead of discharging it to the LRWS. This water is recycled back when pool level is low, reducing the amount of waste water to be processed by the LRWS. This design feature also applies to Objective 3.

The use of underground or buried piping is minimized to the extent practicable. The portions of PCWS pool surge control subsystem piping that are embedded underground or in a yard area pipe chase include guard pipe, reducing the potential for contamination of the environment. This design feature also applies to Objective 4.

ctive 2 - Provide leak The RWDS sumps located in the RXB are equipped with level transmitters to detect ction capability leakage.

Although the SCWS is normally at a higher pressure than the PCWS, radiation detectors are provided in the site cooling water system to detect PCWS heat exchanger tube leaks into the SCWS.

The PCWS demineralizer cubicle is equipped with a level switch to provide early leakage detection.

The secondary containment tank placed around the PCWS surge control tank is equipped with leak detection capabilities. The secondary tank is covered and leak-proof. The secondary containment tank drain sump is also equipped with a level sensor that provides indication of potential leaks from the PCWS surge control storage tank or the piping located in the secondary tank.

The PCWS is configured with pressure, flow, temperature, and conductivity instrumentation to monitor process conditions and to assist in identifying system leaks.

ctive 3 - Reduce Temperature transmitters upstream of the PCWS demineralizers protect the resin amination to minimize from being exposed to high temperature, preventing the damage of resins and ases, cross-contamination reducing waste generation.

waste generation The PCWS demineralizers and resin traps are provided with flushing capability to reduce the contamination levels within the system. This design feature also applies to Objective 4.

The PCWS filters and demineralizers remove impurities and minimize pool contamination. The PCWS has the capability to recycle the pool water after being filtered and demineralized. This feature reduces waste generation.

cale US460 SDAA 12.3-61 Revision 1

Objective Design Features ctive 4 - Facilitate The PCWS components are above ground and usage of long or embedded pipe is ommissioning minimized. This design prevents ground contamination and facilitates decommissioning.

The PCWS components are designed for the 60-year design life of the plant and are designed, to the extent practicable, as discreet assemblies to facilitate decommissioning.

ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-62 Revision 1

Objective Design Features ctive 1 - Minimize the The PLDS has leak channels under the pool floor liner weld seam and attached to the ntial for leaks or spills and pool walls to guide pool leaks to a drain header that leads to RWDS sumps. The ide containment areas PLDS uses welded channels and piping to minimize potential for leaks. Pool leaks are designed to flow through the leak channels to the RWDS sumps.

The PLDS uses stainless steel material or equivalent corrosion resistant materials to prevent corrosion. This feature reduces the potential for leaks. This design feature also applies to Objective 3.

ctive 2 - Provide leak The RWDS sumps, located in the RXB, are equipped with level transmitters to detect ction capability leakage from the pool.

ctive 3 - Reduce The PLDS is designed with corrosion resistant materials for the wetted parts (leak amination to minimize channels, piping, and valves). The selected material is compatible with the operating ases, cross-contamination environment of the pool water.

waste generation ctive 4 - Facilitate The PLDS is designed for the 60-year design life of the plant. The PLDS components ommissioning are above ground to the extent practicable. This design feature facilitates decommissioning.

ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-63 Revision 1

System Objective Design Features ctive 1 - Minimize the The PSS uses proven materials to minimize leaks and contamination of the facility ntial for leaks or spills and and the environment. Welded construction is used as appropriate to minimize the ide containment areas potential for leakage from contaminated systems.

Reactor coolant samples are routed to the sample stations located in the chemistry hot lab for grab sample collection during normal operations. This design feature minimizes the potential for spills of samples in the RXB. In addition, the PSS is designed with minimum embedded or buried piping. The contaminated lines are routed through the pipe chases as much as practicable.

The chemistry hot lab houses sample panels used for collecting reactor coolant grab samples. The purged sample is returned to the CVCS, and excess grab sample is drained into a sink that is hard piped to the RWDS. This design feature minimizes potential for leaks in the RXB.

The floors are sloped to direct leakages or spills to the drain hubs leading to a sump in the RWDS. The slopped floors include the chemistry hot lab and other locations where sample panels are located in the RXB. This design approach prevents spread of contamination and contains the leakages.

The PSS grab sample panels located in the chemistry hot lab of the RXB are equipped with a hood to minimize the airborne contamination and radioactive gases from grab samples. The hood discharges the gases into the RXB ventilation system.

ctive 2 - Provide leak Area radiation monitors are provided in the chemistry hot lab and in areas where ction capability sample panels are located in the RXB.

The PSS is designed with minimum embedded or buried piping to ensure potential leaks can be identified.

Process radiation monitors provided in the non-radioactive interfacing systems provide leak detection capability.

ctive 3 - Reduce The PSS components are designed with materials that are compatible with the amination to minimize operating environment. The wetted parts of piping, valves, pump, heat exchangers, ases, cross-contamination analyzers, grab sample containers, instrumentation, and controls re made of stainless waste generation steel material to prevent corrosion.

The automatic samples are returned back to the originating system as much as practicable to minimize waste generation.

The grab sample panel located in the chemistry hot lab of the RXB is equipped with a hood to remove contaminated gases from the grab samples and discharge these gases to the RBVS.

The PSS is designed with sample sinks to collect the excess of radioactive grab samples and transfer the drainage by gravity to the RWDS. These drains are hard piped to minimize leakage and cross contamination.

Pipe connections to the clean systems are provided with adequate isolation capability and backflow prevention to prevent cross-contamination.

The use of proven materials and welded construction for the piping and components minimizes leakage and unintended contamination of the facility and the environment.

The PSS design includes the capability to isolate sample lines to mitigate the potential spread of contamination.

The PSS sample sink is provided with flush water to clean the sink and flush the drain lines to the RWDS.

ctive 4 - Facilitate The PSS components are designed for the 60-year design life of the plant to the ommissioning extent practicable,with easily removable elements during decommissioning.

The PSS is designed with minimal embedded or buried piping. The contaminated lines are routed through the pipe chases as much as practicable.

cale US460 SDAA 12.3-64 Revision 1

Objective Design Features ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-65 Revision 1

Ventilation, and Air Conditioning System Objective Design Features ctive 1 - Minimize the Periodic in-place testing of the atmospheric portions of the RBVS is performed in ntial for leaks or spills and accordance with RG 1.140 and ASME N510.

ide containment areas The RBVS components are designed, fabricated and tested according to industry codes and standards, and constructed using corrosion resistant materials.

The condensations drains from RBVS components are directed to RWDS drain sumps. This design feature also applies to Objective 3.

ctive 2 - Provide leak The RWDS sumps located in the RXB have level transmitters to detect leakage.

ction capability The RBVS radiation monitors detect potential airborne contamination.

ctive 3 - Reduce The RBVS maintains the RXB atmosphere at a negative pressure relative to the amination to minimize outside environment to prevent potentially contaminated air from leaking to the ases, cross-contamination environment.

waste generation The AHUs and fan coil units have filters to reduce the potential contamination levels of the air.

The RBVS maintains air flow from areas of lesser potential contamination to areas of greater potential contamination to minimize the spread of contamination.

ctive 4 - Facilitate Smooth finished material is used as much as practicable for the equipment to ommissioning minimize contamination of equipment and facilitates decommissioning.

The RBVS exhaust ducts consist of straight runs and long radius elbows wherever possible to reduce the buildup of contaminated particulate.

ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-66 Revision 1

Water System Objective Design Features ctive 1 - Minimize the The reactor component cooling water system (RCCWS) is expected to be free of ntial for leaks or spills and gamma-emitting radionuclides during normal operation but may contain tritiated ide containment areas water. The closed-loop system consists of piping and equipment that are made of stainless steel that is compatible with the RCCWS operating environment. This feature minimizes corrosion and potential leaks. This design feature also applies to Objective 3.

The RCCWS is located in the RXB with sloped floors that direct drainage to the nearest drain hub. This design feature also applies to Objective 3.

ctive 2 - Provide leak The RCCWS is provided with radiation monitors downstream of loads that have a ction capability potential for a radioactive leak to detect cross contamination.

The RCCWS drain tank has radiation monitoring and level instrumentation to provide indications of a leak.

The SCWS has radiation monitors to detect cross-contamination from RCCWS heat exchanger leaks into the system.

ctive 3 - Reduce The RCCWS components are selected for reliable service for the 60-year design life amination to minimize of the plant.

ases, cross-contamination The RCCWS is a closed-loop system that provides an intermediate cooling system waste generation between potentially radioactive heat loads and rejection of heat to the environment via the SCWS. The use of RCCWS as an intermediate cooling loop reduces the potential for releasing contamination.

The RCCWS acts as an intermediate, closed-loop cooling system between radioactive systems and the non-radioactive SCWS. This design provides an additional barrier to ensure that potential contamination is contained within the RXB.

ctive 4 - Facilitate The RCCWS piping and equipment are made of stainless steel material to minimize ommissioning degradation and particulate generation to facilitate decontamination and decommissioning. The DWS can be used for cleaning and flushing purposes to remove contamination.

ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-67 Revision 1

Objective Design Features ctive 1 - Minimize the The RCS is entirely contained within the RPV, which is an ASME Boiler and Pressure ntial for leaks or spills and Vessel Code Section III, Class 1 vessel, and is periodically inspected according to the ide containment areas applicable portions of ASME Section XI (Section 5.2.4).

The RCS components are designed for the 60-year design life of the plant using nuclear industry-proven materials compatible with the operating environment. This also applies to Objective 4.

ctive 2 - Provide leak Reactor coolant system leaks into the SG are detected by radiation monitors ction capability associated with the MSS or the CARS. Leakage monitoring for the SGs is in accordance with EPRI 97-06 (Section 5.4.1).

The CES interfaces with the CNV and is used to detect leakage from the reactor coolant pressure boundary to satisfy GDC 30 (Section 5.2.5).

The CVCS provides the capability to inject argon into the RCS, which increases the sensitivity to detect SG tube leaks using argon-41.

ctive 3 - Reduce The CVCS filters and demineralizers are used to filter and clean the primary coolant, amination to minimize reducing the contamination levels in the RCS.

ases, cross-contamination Materials used in the RCS are low in nickel and cobalt content, to the maximum extent waste generation practical, to reduce contamination due to crud.

The CVCS provides the capability to inject zinc into the RCS to help reduce corrosion product generation and deposition.

ctive 4 - Facilitate Sharp geometric discontinuities and recesses have been avoided to the extent mmissioning practical in the RCS design in order to minimize flow dependent pressure loss and to minimize regions where activated corrosion products can accumulate. This design feature facilitates decommissioning.

The RCS is designed as part of a module that facilitates decommissioning.

ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL Item ronmental monitoring cale US460 SDAA 12.3-68 Revision 1

Heating, Ventilation, and Air Conditioning System Objective Design Features ctive 1 - Minimize the The RWBVS components are designed, fabricated, and tested according to industry ntial for leaks or spills and codes and standards, and constructed using corrosion-resistant materials.

ide containment areas The condensation drains from RWBVS components are directed to RWDS drain sumps. This design feature also applies to Objective 3.

ctive 2 - Provide leak The RWBVS radiation monitors detect potential airborne contamination.

ction capability The RWDS sumps located in the RWB have level transmitters to detect leakage.

ctive 3 - Reduce The RWBVS maintains the RWB atmosphere at a negative pressure relative to the amination to minimize outside environment to prevent potentially contaminated air from leaking to the ases, cross-contamination environment.

waste generation The RWBVS maintains air flow from areas of lesser potential contamination to areas of greater potential contamination to minimize the spread of contamination.

ctive 4 - Facilitate Smooth finished material is used as much as practicable for the equipment to ommissioning minimize contamination of equipment and facilitate decommissioning.

The RWBVS piping and ductwork are above ground. This design feature facilitates decommissioning.

ctive 5 - Operating COL item rams and documentation ctive 6 - Site Radiological COL item ronmental Monitoring cale US460 SDAA 12.3-69 Revision 1

Objective Design Features ctive 1 - Minimize the The RWB equipment rooms are designed with curbs, sump pits, and stainless steel ntial for leaks/ spills and liners in tank cubicles. These features minimize the spread of contamination. This ide containment areas design feature also applies to Object 3.

ctive 2 - Provide leak Objective 6 ction capability ctive 3 - Reduce The RXB is connected to the RWB via various subgrade and above grade aisle ways, amination to minimize chases, duct banks, or vestibules for utility and personnel access.

ases, cross-contamination SRW and LRW tank rooms containing radioactive liquids are lined with stainless steel aste generation in sufficient height to contain the failure of any single vessel or piece of equipment to support contamination minimization.

The RWB design incorporates the separation of non-radiological activities/functions from the radiologically controlled activities and functions as most of the radiological activities are contained below-grade in a concrete structure which also controls airborne radioactivity, while the non-radiological functions are above-grade.

ctive 4 - Facilitate Liners or durable, deep penetrating, smooth-finish coatings are used for below-grade ommissioning structures. This feature applies to the interior surface up to the grade level for floors and walls that form a boundary to the exterior.

Structural surfaces with the potential for radioactive contamination are protected with a smooth coating of infused epoxy or equivalent and waterproofed or stainless steel lining to minimize absorption of contaminants ctive 5 - Operating COL item rams and documentation ctive 6 - Site Radiological COL item ronmental Monitoring cale US460 SDAA 12.3-70 Revision 1

System Objective Design Features ctive 1 - Minimize the The RWDS uses proven materials and welded construction for the system ntial for leaks or spills and components. This design feature reduces the potential for leaks, including the sump ide containment areas liners.

Each sump has two pumps and a level instrument to facilitate automated pump starting and stopping. This design approach reduces the potential of sump overflow and the spread of contamination.

ctive 2 - Provide leak For rooms that are expected to have high radiation, or are normally sealed, there is an ction capability isolation valve and level switch downstream of the floor drain.

The RWDS sump tanks have leak detection capability in the interstitial space between the sump tank and the stainless steel lined concrete sump.

ctive 3 - Reduce The RWDS components are selected for reliable service for the 60-year design life of amination to minimize the plant, reducing waste generation from replacing components.

ases, cross-contamination Loop seals have been provided at various elevations of the RXB and RWB to prevent waste generation air cross-contamination between the floors and the rooms with a common drain header.

The chemical drain tank has a conical bottom design to reduce crud buildup.

The process piping containing contaminated fluid is sloped to facilitate flow and reduce fluid traps. The transfer pumps in the RWDS have check valves in their discharge lines to prevent backflow from another sump or tank contaminating other sumps or systems.

The RWDS equipment is made of stainless steel that is corrosion resistant with smooth surfaces to facilitate decontamination at the end of decommissioning in compliance with 10 CFR 20.1406 This design feature also applies to Objective 4.

To the maximum extent possible, drain lines carrying radioactive waste are welded construction in order to minimize leaks, crud traps and hot spots.

The RWDS sump tanks are strategically located to collect floor and equipment drains from various sources. The drains are segregated (floor, equipment, chemical, RCCWS, and detergent drains) for different handling and processing requirements to minimize cross-contamination.

Equipment and floor drain sump tanks and other RWDS drain tanks are vented to the buildings HVAC exhaust systems to preclude airborne contamination.

Upon detection of high radiation in the RCCWS drain tank, the plant control system alarms and interlock closes the valve back to the RCCWS expansion tank. High radiation in the RCCWS drain tank is the result of contamination of the RCCWS fluid and must be investigated.

The RWDS drain lines and leak detection piping are sloped, atmospheric, gravity flow drain lines.

With exception of RCCWS, the RWDS is not connected to nonradioactive systems in order to prevent inadvertent transfer of contaminated fluids to non-contaminated systems, in compliance with 10 CFR 20.1406.

ctive 4 - Facilitate The RWDS is designed with minimum embedded piping, as much as practicable. The mmissioning use of embedded piping is limited to the RWDS drain lines in the RXB and RWB basemats and the RXB elevation 100 floor slab, as well as the PLD channel drainage lines.

Headers with multiple connected drain lines can be cleaned out via cleanout connections or the floor drains themselves, in accordance with generally recognized plumbing practice. Demineralized water can be temporarily connected to the cleanout connection and used to flush and unplug the lines if needed.

cale US460 SDAA 12.3-71 Revision 1

Objective Design Features ctive 5 - Operating COL item rams and documentation ctive 6 - Site Radiological COL item ronmental Monitoring cale US460 SDAA 12.3-72 Revision 1

Objective Design Features ctive 1 - Minimize the The RXB equipment rooms are designed with curbs and shielded cubicles. This ntial for leaks/ spills and feature minimizes the spread of contamination. (Also applies to Objective 3) ide containment areas ctive 2 - Provide leak Objective 6 ction capability ctive 3 - Reduce The RXB is connected to the RWB via various subgrade and above grade aisle ways, amination to minimize chases, duct banks or vestibules for utility and personnel access.

ases, cross-contamination aste generation ctive 4 - Facilitate Liners or durable, deep penetrating, smooth-finish coatings are used for below-grade ommissioning structures. This feature applies to the interior surface up to the grade level for floors and walls that form a boundary to the exterior.

Structural surfaces with the potential for radioactive contamination are protected with a smooth coating of infused epoxy or equivalent and waterproofed or stainless steel lining to minimize absorption of contaminants ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-73 Revision 1

Objective Design Features ctive 1 - Minimize the The SCWS is normally a clean (non-radioactive) system that supplies cooling water to ntial for leaks/ spills and heat loads in the RXB, Central Utility Building, and the TGB. The SCWS piping that is ide containment areas underground is concrete pipe or stainless steel A316/316L designed to American Water Works Association standards. The SCWS piping that is above ground is made of carbon steel designed to ASME B31.1. This material minimizes corrosion and reduces the potential for leaks. This design feature also applies to Objective 3.

ctive 2 - Provide leak The possibility of radioactive contamination occurs when a heat exchanger leaks.

ction capability Radiation monitors are located directly downstream of RXB heat exchangers, and the cooling tower blowdown line before release to the environment.

Grab sampling capability is provided to measure radiation contamination levels in the system.

ctive 3 - Reduce Radiation monitors that detect leaking heat exchangers have operator actuated amination to minimize isolation valves, except in cooling tower blowdown where isolation is automated in the ases, cross-contamination event of the detection of radiation.

aste generation ctive 4 - Facilitate Site cooling water system components that interface with systems that have the ommissioning potential to contain radioactive materials have provisions for isolation from SCWS and drains within the isolation boundary that are directed to the liquid radwaste system.

The SCWS components are selected for reliable service for the 60-year design life of the plant.

ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL item ronmental monitoring cale US460 SDAA 12.3-74 Revision 1

System Objective Design Features ctive 1 - Minimize the The low activity phase separator tanks and the high activity SRSTs are designed with ntial for leaks or spills and stainless steel material and welded construction to minimize degradation over the life ide containment areas of the plant due to corrosion.

The HEPA filter, downstream of the dewatering fill head vent and the Compactor vent, captures radioactive particles before discharging to the RWBVS.

The high and low activity waste storage areas (Class A and B) are designed with epoxy-coated floors and drainpipes to direct drainage to a floor drain sump for collection and subsequent pumping to the LRWS for treatment and release to the environment.

Tank cubicles, in which contaminated materials are handled and stored, have lined stainless steel walls and floors to contain the whole tank content if a leak develops.

The floors are sloped to direct leakage to a low point floor drain in the tank room for ease of transfer and cleaning. Drain lines direct floor drains to the local sump tanks, which are equipped with level switches to detect liquid accumulation and pumps are provided to transfer the fluid to the LRWS for proper treatment.

The SRWS is designed with above-ground piping to the extent practical. Buried or embedded piping is minimized. In the event that buried or embedded piping cannot be avoided, double-wall piping is used.

ctive 2 - Provide leak Four resin storage tanks are designed with vibrating fork level switches and radar ction capability level transmitters to provide reasonable assurance of the integrity of the SSC. Leak detection (level switches) is located in each tank cubicle and provides alarm to warn the operators of leaks.

Video monitoring is provided in the high and low activity waste storage area for waste handling operation and to monitor for container leakages.

The fill head is designed with a local control panel with closed-circuit television and level indication to monitor HIC level during the resin transfer and dewatering operations. The closed-circuit television in the dewatering room monitors external leakages associated with HIC overflow or hose or joint failures in the dewatering room.

ctive 3 - Reduce The SSC are designed with life-cycle planning using nuclear, industry-proven amination to minimize materials compatible with the chemical, physical, and radiological environment, thus ases, cross-contamination minimizing cross-contamination and waste generation.

waste generation The process piping containing contaminated slurry is sized properly to facilitate easier flow and with sufficient velocity to prevent settling. The piping is designed to reduce fluid traps, thus reducing the decontamination needs and waste generation.

Decontamination fluid is collected and routed to the LRWS for processing and release.

Utility connections are designed with a minimum of two barriers (double isolation valves) to prevent contamination of non-radioactive systems from potentially radioactive systems.

An air gap between the storage tank vent piping and the vent hood minimizes contamination from entering the RWBVS.

ctive 4 - Facilitate The SSC are designed for the 60-year design life and are fabricated, to the maximum ommissioning extent practicable, as individual assemblies for removal.

The SSC are designed with decontamination capabilities. Design features, such as welding techniques and surface finishes, are included to minimize the need for decontamination and minimize waste generation.

Instruments that interface with contaminated fluid or slurry are designed with diaphragm seals to reduce decontamination requirements during decommissioning.

cale US460 SDAA 12.3-75 Revision 1

Objective Design Features ctive 5 - Operating COL item rams and documentation ctive 6 - Site Radiological COL item ronmental Monitoring cale US460 SDAA 12.3-76 Revision 1

Objective Design Features ctive 1 - Minimize the The UHS pool liner plates and the piping system are designed and fabricated ntial for leaks/ spills and according to industry codes and standards. This feature minimizes the potential for ide containment areas leaks. This design feature also applies to objective 3 for cross contamination.

The UHS uses stainless steel makeup line material to reduce the potential that corrosion results in leaks. This feature also applies to Objective 3.

ctive 2 - Provide leak Pool level instrumentation is provided to monitor the pool level.

ction capability The PLDS is designed to collect and detect pool liner leakage. The PLDS leak channels drain potential pool liner leakage to the RWDS sumps located in the RXB, which are equipped with level transmitters to detect leaks. The PLDS also provides for a manual leak measurement capability for each leak channel to quantify small leaks (i.e., few gallons per week).

ctive 3 - Reduce Stainless steel is selected as the material for wetted components to provide corrosion amination to minimize resistance and minimize degradation and particulate generation over the 60-year ases, cross-contamination design life of the plant. (also applies to objective 4) waste generation The water inventory within the UHS is provided with cleanup capability through the PCUS filters and demineralizers to reduce the contamination level of the water.

ctive 4 - Facilitate The UHS components are designed to facilitate decommissioning with stainless steel mmissioning surfaces for easier decontamination.

ctive 5 - Operating COL item rams and documentation ctive 6 - Site radiological COL Item ronmental monitoring cale US460 SDAA 12.3-77 Revision 1

Objective Design Features ctive 1 - Minimize the Piping and component materials in the UWS are consistent with a 60-year design life.

ntial for leaks/ spills and Valve material(s) are consistent with system service(s) and design conditions. UWS ide containment areas piping is designed to ASME B31.1. The majority of the UWS is 304 stainless steel for above ground piping and HDPE for underground piping. The SCWS blowdown piping is carbon steel for above ground piping and 316 stainless steel for underground piping. The 316 stainless steel material is used for the underground piping penetrating through building slabs.

ctive 2 - Provide leak The UWS is the single-point liquid effluent release path to the environment, and it is ction capability sampled and monitored for radiation. An off-line radiation monitor provides continuous indication of effluent parameters.

ctive 3 - Reduce The above and below ground UWS piping is designed to last for 60 years. Adequate amination to minimize space is provided for maintenance of equipment and other system components in the ases, cross-contamination system layout and design. Additionally, the raw water pumps and supply pumps are aste generation provided with redundant pumps to allow for one pump to be taken out of service for maintenance. Each pump has an upstream and downstream isolation valve to enable separation from the system for maintenance, replacement, or both.

ctive 4 - Facilitate The UWS discharge basin may become contaminated during operation and can be ommissioning decontaminated during decommissioning.

ctive 5 - Operating COL Item rams and documentation ctive 6 - Site radiological COL Item ronmental monitoring cale US460 SDAA 12.3-78 Revision 1

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-1a: Reactor Building Radiation Zone Map - 25' Elevation

(( Withheld - See Part 9 NuScale US460 SDAA 12.3-79 Revision 1

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-1b: Reactor Building Radiation Zone Map - 40 Elevation (( Withheld - See Part 9 }} NuScale US460 SDAA 12.3-80 Revision 1

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-1c: Reactor Building Radiation Zone Map - 55' Elevation (( Withheld - See Part 9 }} NuScale US460 SDAA 12.3-81 Revision 1

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-1d: Reactor Building Radiation Zone Map - 70' Elevation (( Withheld - See Part 9 }} NuScale US460 SDAA 12.3-82 Revision 1

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-1e: Reactor Building Radiation Zone Map - 85' Elevation (( Withheld - See Part 9 }} NuScale US460 SDAA 12.3-83 Revision 1

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-1f: Reactor Building Radiation Zone Map - 100' Elevation (( Withheld - See Part 9 }} NuScale US460 SDAA 12.3-84 Revision 1

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-1g: Reactor Building Radiation Zone Map - 126' Elevation (( Withheld - See Part 9 }} NuScale US460 SDAA 12.3-85 Revision 1

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-1h: Reactor Building Radiation Zone Map - 145' 6" Elevation (( Withheld - See Part 9 }} NuScale US460 SDAA 12.3-86 Revision 1

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-2a: Radioactive Waste Building Radiation Zone Map - 70' Elevation (( Withheld - See Part 9 }} NuScale US460 SDAA 12.3-87 Revision 1

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-2b: Radioactive Waste Building Radiation Zone Map - 82' Elevation (( Withheld - See Part 9 }} NuScale US460 SDAA 12.3-88 Revision 1

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-2c: Radioactive Waste Building Radiation Zone Map - 100' Elevation (( Withheld - See Part 9 }} NuScale US460 SDAA 12.3-89 Revision 1

The dose assessment information in this section includes the estimated radiation exposures to plant personnel performing work activities involving normal operations, maintenance, inspections, refueling activities, and waste handling, using the methodology presented in Regulatory Guide 8.19 to demonstrate the facility design complies with 10 CFR 20. The dose assessment process during the design of the plant and the program for keeping doses as low as reasonably achievable (ALARA) help maintain occupational radiation exposures ALARA. To estimate the occupational radiation exposures (OREs) for the facility, various work activities and durations are compiled along with the expected significant (>0.1 mrem/hr) radiation fields that are encountered. 4.1 Occupational Radiation Exposure Regulatory Guide 8.19 methodology is used to determine the OREs to plant personnel. Section 12.3 describes radiation protection design features and Section 12.5 explains elements of the operational radiation protection program. Both the program and design maintain operator occupational radiation exposure ALARA. Section 12.2 provides the airborne concentration in various parts of the facility. The calculated occupational exposure estimates are developed to reflect the expected dose rates in a facility during its operation. In the absence of operational dose information, the sources in Section 12.2 are used to inform some of the assumed dose rates used for occupational exposures. The following activity categories are used to calculate the estimated annual ORE estimates:

  • reactor operations and surveillances
  • routine maintenance
  • inservice inspection
  • special maintenance
  • waste processing
  • refueling activities Table 12.4-1 summarizes the total estimated annual occupational personnel doses.

Major elements contributing to lower occupational doses include low plant radiation fields due to crud reduction efforts and leak minimization, favorable plant arrangement and equipment layout, and operational practices and procedures that minimize time spent in radiation fields. The paragraphs below detail each work activity associated with annual ORE. cale US460 SDAA 12.4-1 Revision 1

During plant operations, systems and components are monitored for performance and operating condition. Some examples of the specific activities performed by operators include:

  • inspection and performance tests of plant components and systems
  • checks of unidentified leaks
  • operation of manual valves
  • reading of instruments
  • health physics patrols and surveys
  • security sweeps or patrols
  • calibration of electrical and mechanical equipment
  • chemistry sampling and analysis Table 12.4-2 provides estimated values of the collective doses for reactor operations and surveillances.

4.1.2 Routine Inspection and Maintenance During plant operations, routine inspection and maintenance activities include various inspections, repairs, and replacements of pumps, valves, heat exchangers, and instrumentation within the Reactor Building and the hot machine shop. Table 12.4-3 provides occupational dose estimates from routine inspection and maintenance. 4.1.3 Inservice Inspection Periodic inservice inspections are required for safety-related equipment by the American Society of Mechanical Engineers Boiler and Pressure Vessel Code, Section XI. These components include the reactor pressure vessel, containment vessel, core support, and other internal components. These inspections are typically performed during refueling outages. Table 12.4-4 provides occupational dose estimates from inservice inspection (ISI) activities. 4.1.4 Special Maintenance Special maintenance consists of activities that go beyond routine scheduled maintenance, including the modification of equipment to upgrade the NuScale Power Module (NPM) and repairs to failed components. The maintenance activities included in this evaluation are associated with the upper section of the NPM while staged in the dry dock during refueling outages. Maintenance activities that do not require a shutdown are considered to be routine maintenance activities. Some special maintenance activities for each NPM are assumed to cale US460 SDAA 12.4-2 Revision 1

4.1.5 Waste Processing The waste processing occupational dose estimate includes activities involving the processing of liquid, solid, and gaseous radioactive wastes and other activities in the Radioactive Waste Building, including routine inspections and maintenance and operations and surveillance activities. The doses are estimated based on identified activities that are grouped into three categories: waste management, waste maintenance, and other activities. Waste management activities include the collection, processing, storing, and releasing of radioactive waste. Waste maintenance activities include system equipment inspections and repair, component flushing, and component replacement. Other activities are support activities within the Radioactive Waste Building, including chemistry sampling, instrument calibrations, health physics surveillances, and security patrols. Table 12.4-6 lists the estimated occupational doses from waste processing. 4.1.6 Refueling Activities, Including Dry Dock Outage Activities When an NPM is shut down for refueling, other NPMs continue operation. Therefore, dose contributions from operating NPMs are included with the dose received from outage activities, as appropriate. In addition, station personnel could be tasked with working on multiple NPM refueling outages within the same year. The dose assessment for refueling activities includes the following major activities:

  • preparing the NPM for movement
  • disconnecting and moving the NPM to the containment flange tool
  • disassembling the NPM and dry dock activities
  • completing the lower containment vessel work
  • refueling the reactor
  • reassembling and moving the NPM to the operating bay
  • reconnecting the NPM
  • transitioning the NPM to power operations Table 12.4-7 provides estimated occupational doses from refueling activities.

4.1.7 Overall Plant Doses Occupational personnel dose estimates are calculated assuming a 6-NPM site and an 18-month fuel cycle for NPM operation, which equates to four refueling cale US460 SDAA 12.4-3 Revision 1

above. 4.1.8 Post-Accident Actions There are no vital areas, as defined by NUREG-0737, Item II.B.2, other than the main control room and the technical support center, which are in compliance with 10 CFR 50.34(f)(2)(vii). Chapter 15 defines post-accident operator actions, and there are no credited post-accident actions outside the main control room. Section 15.0.3 provides operator dose assessments for the main control room and the technical support center. 4.1.9 Construction Activities For the construction of an additional NuScale plant adjacent to an existing NuScale plant, the estimated annual radiation exposure to a construction worker is estimated based upon a construction staffing plan over the estimated construction period. The annual dose for a construction worker is estimated to be 1.64 mrem/year. L Item 12.4-1: An applicant that references the NuScale Power Plant US460 standard design will estimate doses to construction personnel from a co-located existing operating nuclear power plant that is not a NuScale Power Plant. 4.2 Radiation Exposure at the Restricted Area Boundary The direct radiation to the restricted area boundary from on-site sources, such as buildings, is negligible. cale US460 SDAA 12.4-4 Revision 1

Activity Category Estimated Annual Dose (man-rem) ctor operations & surveillance 2.3 tine maintenance & inspections 3.7 rvice inspection 3.4 cial maintenance 2.7 te processing 1.3 eling 1.7 l 15.1

Estimates assume a plant with 6 NPMs on an 18-month refueling cycle.

cale US460 SDAA 12.4-5 Revision 1

Discipline Exposure Times (man-hr/year) Annual ORE (man-rem) rations 1.5E+03 6.3E-01 lth physics 1.7E+03 7.8E-01 urity 2.9E+03 2.9E-01 ument and controls (I&C) 1.5E+03 6.3E-01 l 7.5E+03 2.3E+00 cale US460 SDAA 12.4-6 Revision 1

Total ORE by Floor Floor Elevation Man Hours Weighted Average Total ORE (ft) (hr) Dose Rate (man-rem) (mrem/hr) 25 4.0E-01 3.9E-01 1.6E-04 40 1.2E02 2.0E-01 2.5E-02 55 1.9E02 4.0E00 7.5E-01 70 4.2E01 1.9E-01 8.1E-03 85 2.3E02 2.1E-01 4.9E-02 100 1.1E03 2.6E+00 2.9E+00 Total 1.7E03 2.2E+00 3.7E+00

Estimates assume a plant with 6 NPMs on an 18-month refueling cycle.

cale US460 SDAA 12.4-7 Revision 1

Activity Exposure Time Average Dose Rate ORE (man-rem/year) (man-hours/year) (rem/hr) nside containment 3.2E+02 2.1E-03 6.8E-01 utside containment 2.6E+02 1.5E-03 3.8E-01 m generator ISI 1.1E+02 2.1E-02 2.4E+00 l 6.9E+02 5.0E-03 3.5E+00

Estimates assume a plant with 6 NPMs on an 18-month refueling cycle.

cale US460 SDAA 12.4-8 Revision 1

ORE by Type Exposure Time Average Dose Rate ORE (man-rem) (man-hours/year) (rem/hr) prep and clean-up 3.0E+02 3.8E-03 1.1E+00 k testing 2.2E+02 2.1E-03 4.6E-01 trol rod drive 3.4E+01 6.2E-03 2.1E-01 hanism replacement surizer heater 3.1E+01 4.0E-03 1.2E-01 ection and replacement nsertion, retraction, and 4.8E+01 5.4E-03 2.6E-01 acement sor maintenance 4.0E+01 1.1E-02 4.5E-01 ube plugging and 2.1E+00 1.9E-02 3.9E-02 ndary-side chemical ning l 6.7E+02 3.9E-03 2.7E+00

Estimates assume a plant with 6 NPMs on an 18-month refueling cycle.

cale US460 SDAA 12.4-9 Revision 1

Activity Average Dose Exposure Time Estimated Annual Rate (mrem/hr) (man-hr/year) Dose (man-rem) te management 4.5E-01 4.5E+02 2.0E-01 te maintenance 8.8E-01 2.6E+02 2.3E-01 r waste activities 4.0E-01 2.2E+03 8.8E-01 l 4.5E-01 2.9E+03 1.3E+00

Estimates assume a plant with 6 NPMs on an 18-month refueling cycle.

cale US460 SDAA 12.4-10 Revision 1

Refueling Activity Exposure Time per Average Dose Rate Annual Total ORE year (man-hrs) (rem/hr) from Refueling (man-rem/year) ldown and cleanup 3.2E+01 8.3E-04 2.6E-02 ule disconnect/movement 3.2E+02 2.5E-03 7.9E-01 ssembly 0.0E+00 0.0E+00 0.0E+00 er containment work window 0.0E+00 0.0E+00 0.0E+00 el work window 0.0E+00 0.0E+00 0.0E+00 ssembly 0.0E+00 0.0E+00 0.0E+00 onnection 3.4E+02 2.6E-03 8.6E-01 t-up to hot standby 6.4E+01 9.7E-04 6.2E-02 ueling Total 7.5E+02 2.3E-03 1.7E+00

Estimates assume a plant with 6 NPMs on an 18-month refueling cycle, assuming 4 refueling cycles per year.

cale US460 SDAA 12.4-11 Revision 1

L Item 12.5-1: An applicant that references the NuScale Power Plant US460 standard design will describe elements of the operational radiation protection program to ensure that occupational and public radiation exposures are as low as reasonably achievable in accordance with 10 CFR 20.1101. cale US460 SDAA 12.5-1 Revision 1}}

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