ML20036D454

Part 02 - Final Safety Analysis Report (Rev. 4) - Part 02 - Tier 02 - Chapter 12 - Radiation Protection - Sections 12.01 - 12.05

ML20036D454
Person / Time
Site:	NuScale
Issue date:	01/16/2020
From:	Bergman T NuScale
To:	Office of Nuclear Reactor Regulation
Cranston G
References
NUSCALESMRDC, NUSCALESMRDC.SUBMISSION.10, NUSCALEPART02.NP, NUSCALEPART02.NP.4
Download: ML20036D454 (199)

Text

e Standard Plant Certification Application ter Twelve iation Protection T 2 - TIER 2 4

2020 uScale Power LLC. All Rights Reserved

COPYRIGHT NOTICE document bears a NuScale Power, LLC, copyright notice. No right to disclose, use, or copy any of information in this document, other than by the U.S. Nuclear Regulatory Commission (NRC), is horized 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, as well he issuance, denial, amendment, transfer, renewal, modification, suspension, revocation, or ation of a license, permit, order, or regulation subject to the requirements of 10 CFR 2.390 regarding rictions on public disclosure to the extent such information has been identified as proprietary by cale Power, LLC, copyright protection notwithstanding. Regarding nonproprietary versions of e reports, the NRC is permitted to make the number of additional copies necessary to provide ies for public viewing in appropriate docket files in public document rooms in Washington, DC, and where as may be required by NRC regulations. Copies made by the NRC must include this copyright ce in all instances and the proprietary 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 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.1-6 12.2 Radiation Sources . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-1 12.2.1 Contained Sources. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-1 12.2.2 Airborne Radioactive Material Sources. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-8 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 . . . . 12.3-16 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 2 i Revision 4

le 12.2-1: Core and Coolant Source Information. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-11 le 12.2-2: Fission Gamma Energy Spectrum Probability Density Function . . . . . . . . . . . . . . . 12.2-12 le 12.2-3: Cold Leg Primary Coolant Gamma Source Term . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-14 le 12.2-4: Hot Leg Primary Coolant Gamma Source Term . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-16 le 12.2-5: Nitrogen-16 Primary Coolant Concentrations at Full Power . . . . . . . . . . . . . . . . . . . 12.2-18 le 12.2-6: Chemical and Volume Control System Component Source Term Inputs and Assumptions . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-19 le 12.2-7: Chemical and Volume Control System Component Source Terms - Radionuclide Content . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-20 le 12.2-8: Chemical and Volume Control System Component Source Terms - Source Strengths . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-22 le 12.2-9: Reactor Pool Cooling, Spent Fuel Pool Cooling, Pool Cleanup, and Pool Surge Control System Component Source Term Inputs and Assumptions. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-24 le 12.2-10: Reactor Pool Cooling, Spent Fuel Pool Cooling, Pool Cleanup and Pool Surge Control System Component Source Terms - Radionuclide Content . . . . . 12.2-25 le 12.2-11: Reactor Pool Cooling, Spent Fuel Pool Cooling, Pool Cleanup, and Pool Surge Control System Component Source Terms - Source Strengths . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-27 le 12.2-12: Liquid Radioactive Waste System Component Source Term Inputs and Assumptions. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-29 le 12.2-13a: Liquid Radioactive Waste System Component Source Terms - Radionuclide Content. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-31 le 12.2-13b: Liquid Radioactive Waste System Component Source Terms - Radionuclide Content. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-33 le 12.2-14a: Liquid Radioactive Waste System Component Source Terms - Source Strengths . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-35 le 12.2-14b: Liquid Radioactive Waste System Component Source Terms - Source Strengths . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-37 le 12.2-15: Gaseous Radioactive Waste System Component Source Term Inputs. . . . . . . . . . 12.2-39 le 12.2-16: Gaseous Radioactive Waste System Component Source Term Radionuclide Content . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-40 le 12.2-17: Gaseous Radioactive Waste System Component Source Terms - Source Strengths . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-41 le 12.2-18: Solid Radioactive Waste System Source Term Inputs . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-43 le 12.2-19: Solid Radioactive Waste System Component Source Terms - Radionuclide Content. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-44 2 ii Revision 4

le 12.2-20: Solid Radioactive Waste System Component Source Terms - Source Strengths . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-47 le 12.2-21: Spent Fuel Gamma Source Strength . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-49 le 12.2-22: Spent Fuel Neutron Energy Spectrum. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-51 le 12.2-23: In-Core Instrument Source Term Input Assumptions . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-52 le 12.2-24: In-Core Instrumentation Gamma Spectra . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-53 le 12.2-25: Control Rod Assembly Tip Source Term Input Assumptions. . . . . . . . . . . . . . . . . . . 12.2-54 le 12.2-26: Control Rod Assembly Tip Gamma Spectra (End of Cycle 2) . . . . . . . . . . . . . . . . . . . 12.2-55 le 12.2-27: Secondary Neutron Source Gamma Spectra (End of Cycle 1) . . . . . . . . . . . . . . . . . . 12.2-56 le 12.2-28: Post-Accident Equipment Qualification Source Term Input Assumptions. . . . . . 12.2-57 le 12.2-29: Not Used . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-58 le 12.2-30: Not Used . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-59 le 12.2-31: Post-Accident Integrated Energy Deposition and Integrated Dose . . . . . . . . . . . . 12.2-60 le 12.2-32: Input Parameters for Determining Facility Airborne Concentrations. . . . . . . . . . . 12.2-61 le 12.2-33: Reactor Building Airborne Concentrations . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.2-62 le 12.2-34: Maximum Post-Accident Radionuclide Concentrations . . . . . . . . . . . . . . . . . . . . . . . 12.2-65 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: Very High-Radiation Areas (>500 Rad/hr). . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-30 le 12.3-4: Typical Cobalt Content of Materials . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-31 le 12.3-5a: Reactor Building Areas of Potential Airborne Radioactive Material . . . . . . . . . . . . 12.3-32 le 12.3-5b: Radioactive Waste Building Areas of Potential Airborne Radioactive Material. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-33 le 12.3-6: Reactor Building Shield Wall Geometry . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-34 le 12.3-7: Radioactive Waste Building Shield Wall Geometry . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-41 le 12.3-8: Reactor Building Radiation Shield Doors . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-43 le 12.3-9: Radioactive Waste Building Radiation Shield Doors. . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-45 le 12.3-10: Fixed Area and Airborne Radiation Monitors Post-Accident Monitoring Variables. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-46 le 12.3-11: Fixed Airborne Radiation Monitors. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-48 le 12.3-12: Fixed Area Radiation Monitors . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-49 le 12.3-13: NuScale Power Plant Systems with NRC Regulatory Guide 4.21 Evaluation . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-56 2 iii Revision 4

le 12.3-14: Regulatory Guide 4.21 Design Features for Auxiliary Boiler System . . . . . . . . . . . . 12.3-57 le 12.3-15: Regulatory Guide 4.21 Design Features for Balance-of-Plant Drain System . . . . 12.3-58 le 12.3-16: Regulatory Guide 4.21 Design Features for Containment Evacuation System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-59 le 12.3-17: Regulatory Guide 4.21 Design Features for Containment Flooding and Drain System. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-60 le 12.3-18: Regulatory Guide 4.21 Design Features for Condensate and Feedwater System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-61 le 12.3-19: Regulatory Guide 4.21 Design Features for Condensate Polishing System . . . . . 12.3-62 le 12.3-20: Regulatory Guide 4.21 Design Features for Normal Control Room Ventilation System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-63 le 12.3-21: Regulatory Guide 4.21 Design Features for Chemical and Volume Control System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-64 le 12.3-22: Regulatory Guide 4.21 Design Features for Circulating Water System . . . . . . . . . 12.3-66 le 12.3-23: Regulatory Guide 4.21 Design Features for Decay Heat Removal System . . . . . . 12.3-67 le 12.3-24: Regulatory Guide 4.21 Design Features for Gaseous Radioactive Waste System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-68 le 12.3-25: Regulatory Guide 4.21 Design Features for Liquid Radioactive Waste System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-69 le 12.3-26: Regulatory Guide 4.21 Design Features for Main Steam System . . . . . . . . . . . . . . . 12.3-71 le 12.3-27: Regulatory Guide 4.21 Design Features for Pool Cleanup System . . . . . . . . . . . . . 12.3-72 le 12.3-28: Regulatory Guide 4.21 Design Features for Pool Leak Detection System . . . . . . . 12.3-73 le 12.3-29: Regulatory Guide 4.21 Design Features for Pool Surge Control System . . . . . . . . 12.3-74 le 12.3-30: Regulatory Guide 4.21 Design Features for Process Sampling System . . . . . . . . . 12.3-75 le 12.3-31: Regulatory Guide 4.21 Design Features for Reactor Building Heating Ventilation and Air Conditioning System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-76 le 12.3-32: Regulatory Guide 4.21 Design Features for Reactor Component Cooling Water System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-77 le 12.3-33: Regulatory Guide 4.21 Design Features for Reactor Coolant System. . . . . . . . . . . 12.3-78 le 12.3-34: Regulatory Guide 4.21 Design Features for Reactor Pool Cooling System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-79 le 12.3-35: Regulatory Guide 4.21 Design Features for Radioactive Waste Building Heating Ventilation and Air Conditioning System . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-80 le 12.3-36: Regulatory Guide 4.21 Design Features for Radioactive Waste Building . . . . . . . 12.3-81 le 12.3-37: Regulatory Guide 4.21 Design Features for Radioactive Waste Drain System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-82 2 iv Revision 4

le 12.3-38: Regulatory Guide 4.21 Design Features for Reactor Building . . . . . . . . . . . . . . . . . . 12.3-83 le 12.3-39: Regulatory Guide 4.21 Design Features for Site Cooling Water System . . . . . . . . 12.3-84 le 12.3-40: Regulatory Guide 4.21 Design Features for Spent Fuel Pool Cooling System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-85 le 12.3-41: Regulatory Guide 4.21 Design Features for Solid Radioactive Waste System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-86 le 12.3-42: Regulatory Guide 4.21 Design Features for Ultimate Heat Sink System . . . . . . . . 12.3-88 le 12.3-43: Regulatory Guide 4.21 Design Features for Utility Water System . . . . . . . . . . . . . . 12.3-89 le 12.3-44: Regulatory Guide 4.21 Design Features for Demineralized Water System . . . . . . 12.3-90 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 le 12.4-8: Not Used . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12.4-12 2 v Revision 4

re 12.3-1a: Reactor Building Radiation Zone Map - 24' Elevation . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-91 re 12.3-1b: Reactor Building Radiation Zone Map - 35'-8" Elevation. . . . . . . . . . . . . . . . . . . . . . . 12.3-92 re 12.3-1c: Reactor Building Radiation Zone Map - 50' Elevation . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-93 re 12.3-1d: Reactor Building Radiation Zone Map - 62' Elevation . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-94 re 12.3-1e: Reactor Building Radiation Zone Map - 75' Elevation . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-95 re 12.3-1f: Reactor Building Radiation Zone Map - 86' Elevation . . . . . . . . . . . . . . . . . . . . . . . . . 12.3-96 re 12.3-1g: Reactor Building Radiation Zone Map - 100' Elevation . . . . . . . . . . . . . . . . . . . . . . . . 12.3-97 re 12.3-1h: Reactor Building Radiation Zone Map - 126' Elevation . . . . . . . . . . . . . . . . . . . . . . . . 12.3-98 re 12.3-1i: Reactor Building Radiation Zone Map - 146' Elevation . . . . . . . . . . . . . . . . . . . . . . . . 12.3-99 re 12.3-2a: Radioactive Waste Building Radiation Zone Map - 71' Elevation . . . . . . . . . . . . . .12.3-100 re 12.3-2b: Radioactive Waste Building Radiation Zone Map - 100' Elevation. . . . . . . . . . . . .12.3-101 re 12.3-3: NuScale Power Module Monte Carlo N-Particle Shielding Model . . . . . . . . . . . . .12.3-102 re 12.3-4a: Not Used . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .12.3-103 re 12.3-4b: Not Used . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .12.3-104 re 12.3-4c: Not Used . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .12.3-105 re 12.3-4d: Not Used . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .12.3-106 2 vi Revision 4

1 Ensuring that Occupational Radiation Exposures Are as Low as Reasonably Achievable The 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 radiation protection policies, programs and features are described in this chapter.

1.1 Policy Considerations 1.1.1 Design and Construction Policies The commitment to ALARA is demonstrated by processes that implement ALARA radiation protection design criteria in the plant design. The application of ALARA principles occurs throughout the design process. As the design progresses, application of ALARA-related decisions and design features are reviewed and updated, as appropriate, to reflect operating experience and lessons learned. Design reviews are conducted to 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. This integrated approach to the design of structures, systems, and components ensures that exposures to offsite and onsite personnel are ALARA.

1.1.2 Operational Policies Implementation of the operational ALARA policy is addressed in Section 12.1.3.

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 (RGs) 8.8, Revision 3 and 8.10, Revision 1-R. Plant operations policy considerations described in RG 8.8, RG 8.10, and RG 1.8, Revision 3 will be demonstrated by the COL applicant as discussed in Section 12.1.3 and Section 12.5. The design meets the guidance of RG 8.8, Sections C.2 and C.4 that address facility, equipment, and instrumentation design features. Plant features that are examples of compliance with RG 8.8 are addressed in Section 12.3.

1.2 Design Considerations This section describes the methods and features that allow the policy considerations of Section 12.1.1 to be applied. Design features and attributes for maintaining personnel exposures ALARA are presented in Section 12.3.

1.2.1 General Design Considerations for Maintaining Exposures ALARA The design process was conducted by experienced engineers utilizing an inter-discipline ALARA design review process to ensure the design conforms to 10 CFR 20.1101(b) and RG 8.8. The design engineers received training in radiation 2 12.1-1 Revision 4

radiation shielding, radiation zone maps, and occupational radiation exposure estimates. The results of the occupational radiation exposure estimates were provided as feedback to the design engineers during multi-discipline design phase reviews, which were used to develop additional ALARA features, as necessary.

The ALARA philosophy guiding the design is to ensure that 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 The design considerations implemented to minimize production, distribution, and retention of activated corrosion products includes appropriate material selection and proper water chemistry. These design considerations are described in more detail in Section 12.1.2.2.

Design considerations and features addressing 10 CFR 20.1406 to minimize contamination of the facility and the environment, minimize waste generation, and facilitate decommissioning are described in Section 12.3.

1.2.2 Equipment Design Considerations for Maintaining Exposures ALARA 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, with consideration given to potential radiation problems associated with component and materials design. The following paragraphs summarize examples of design considerations utilized in the design to implement ALARA.

1.2.2.2 Equipment Design Considerations to Limit Time Spent in Radiation Areas Equipment is designed with instrumentation and controls in accessible areas during normal and abnormal operating conditions. Equipment is selected to minimize the potential dose to personnel during maintenance. The equipment is provided with drainage capabilities to facilitate maintenance and smooth surfaces to reduce contamination and ease decontamination efforts. Components are chosen for high reliability, ease of maintenance, ease of replacement, accessibility, and ease of decontamination. When possible, components located in higher dose 2 12.1-2 Revision 4

• 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 Site-specific information describing how the plant implements the design consideration guidance provided in RG 8.8 is provided in Section 12.1.3.

1.2.2.3 Equipment Design Considerations to Limit Component Radiation Levels The materials selected for components were chosen to meet service requirements and minimize cobalt-containing materials (e.g., Stellite) coming in contact with the primary coolant system. The cobalt and nickel content and corrosion resistance of a given material influence the production of corrosion products that can become activated. 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. This material selection results in significantly less production of activated corrosion products.

Nickel-based alloys are used in pressurized water reactors due to their excellent corrosion resistance in both reducing and oxidizing environments. Alloy 690 was chosen for the steam generator tubes based on its resistance to primary water stress corrosion cracking and its good heat transfer properties.

The cobalt content of alloy materials is controlled to minimize the radiation exposures resulting from the activation of wear or corrosion products.

Forged low-alloy steel ASME SA-508 is selected for the reactor pressure vessel (RPV) that surrounds the reactor core, pressurizer, and steam generators. For the lower RPV that is subjected to high levels of radiation, copper and phosphorous contents are limited because these elements are primarily responsible for the hardening and embrittlement caused by neutron irradiation.

Equipment is designed with provisions to limit leaks and the plant is designed to collect and control leaked fluid through the use of 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 such as tanks and piping. Piping design avoids the creation of stagnant legs, uses sloping pipe runs, and locates connections above 2 12.1-3 Revision 4

The liquid radioactive waste system is provided with a clean-in-place skid that allows flushing of system components with demineralized water, as needed.

1.2.2.4 Water Chemistry Reactor water chemistry is controlled during operation to minimize corrosion of surfaces in contact with the coolant and minimize the production of activated corrosion products. For reactivity control, boric acid is added as a soluble neutron poison. To maintain the reactor coolant at a slightly alkaline pH, enriched lithium-7 hydroxide is added to the coolant.

To maintain a reducing environment in the reactor coolant, dissolved hydrogen is added, thus minimizing oxidation and suppressing radiolytic oxygen generation during operation. During startup, oxygen removal is accomplished by a combination of mechanical degasification and chemical degasification using hydrazine. Zinc may also be added to reduce corrosion product transport.

Impurities and suspended solids are removed from the reactor coolant by the chemical and volume control system.

1.2.3 Facility Layout General Design Considerations for Maintaining Radiation Exposures ALARA 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 Annex Building, and include change rooms, offices, calibration facilities, counting room, hot machine shop, and equipment and personnel decontamination facilities. The Annex 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 utilized in minimizing personnel time spent in radiation areas include:

• space is provided within cubicles for a laydown area for special tools and ease of servicing activities

• instrumentation readouts, monitors, and control points are 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 2 12.1-4 Revision 4

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 is provided between components

• labyrinth entrances are provided to reduce radiation streaming out of cubicle entrances

• shield wall penetrations are configured to prevent "line-of-sight" streaming

• pipe chases are used 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

• spare connections on tanks and other components located in high radiation areas are provided to allow for greater operational flexibility

• pumps are selected 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 are provided

• instrumentation is 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 are included

• adequate space for moveable or temporary shielding for sources is provided

• means to control contamination and to facilitate decontamination of potentially contaminated areas are provided

• piping for "clean services" (e.g., station air, potable water, nitrogen, etc.) is located separate from piping for contaminated systems to avoid cross-contamination are provided

• features that permit remote removal, installation, inspection, or servicing of radioactive components are provided

• 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 are provided 2 12.1-5 Revision 4

Item 12.1-1: A COL applicant that references the NuScale Power Plant design certification 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).

2 12.1-6 Revision 4

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

• radiation shielding design calculations

• ventilation systems design

• radwaste systems design, including the classification of structures, systems, and components per Regulatory Guide 1.143

• radiation protection assessment, including personnel protection 2.1 Contained Sources The contained radiation sources are developed for normal operation and shutdown conditions and are based on the design basis primary coolant activity concentrations from Section 11.1. 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 code is used to bin the particle emissions into default energy bins based on the activity of each individual isotope. The radiation sources described in this section provide part of the basis for the design of radiation shielding features. Plan scale drawings showing locations of contained sources are included in the radiation zone maps (Section 12.3).

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.

The fission neutron and fission gamma source strength and neutron energy spectrum information are provided in Table 12.2-1. The n-gamma source strength is internally generated by MCNP6 using the neutron source strength as an input. The fission gamma energy probability density function is provided in Table 12.2-2. 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 design basis source terms are described in Section 11.1.

The contribution of gamma radiation from the primary coolant is comprised of two components: the hot leg (lower riser, and upper riser) and a cold leg (pressurizer, steam generator, and reactor coolant downcomer region). The hot leg is modeled with the peak N-16 concentration in the lower riser, while the cold leg is modeled with an N-16 concentration equal to the entrance of the steam generator. Because of the low 2 12.2-1 Revision 4

uniformly treating the hot leg with the peak N-16 concentration in the RCS loop, and the cold leg uniformly with the steam generator entrance concentration, the gamma contribution from N-16 is conservatively modeled. The fission isotopes and corrosion isotopes (CRUD) are uniformly modeled on a primary coolant mass basis. The primary coolant gamma spectra are provided in Table 12.2-3 and Table 12.2-4.

Nitrogen-16 is present throughout the primary coolant loop, and the modeling simplification described above is conservative from a bioshield radiation shielding perspective. Table 12.2-5 tabulates the nitrogen-16 concentration at several locations in the primary coolant system.

2.1.3 Chemical and Volume Control System The chemical and volume control system (CVCS) takes a portion of the RCS and processes the water through heat exchangers, demineralizers, and filters. The treated primary coolant water 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 assumed to be 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 assumed to be in operation for one-half of the fuel cycle because they are operated intermittently during the operating cycle for lithium removal. The decontamination factors assumed are listed in Table 12.2-6.

The CVCS demineralizer beds are located in the Reactor Building (RXB) on the 24' elevation inside the CVCS cubicles. The mixed-bed source terms and source strengths are listed in Table 12.2-7 and Table 12.2-8, respectively. These source terms and the associated analyses do not include short-term transients such as CRUD bursts associated with refueling outages. Based on an assumed Co-58 peaking factor of 10,000 and an assumed peaking factor of 1,000 for other CRUD isotopes, it is estimated that a CRUD burst could add up to 450 curies of CRUD isotopes to the CVCS mixed bed demineralizer. This results in the estimates of activity within some plant SSCs to not reflect the CRUD burst related activity, including the CVCS mixed bed demineralizer values (both columns) in Table 12.2-7 and Table 12.2-8.

Regenerative and Non-Regenerative Heat Exchangers The regenerative heat exchanger is used to cool the primary coolant as it enters the CVCS using the CVCS water returning back to the RCS. The non-regenerative heat exchanger further cools the primary coolant, using reactor component cooling water, to protect the demineralizer resins. The heat exchangers are tube and shell type, as described in Section 9.3.4. To calculate the radiological source term, the heat 2 12.2-2 Revision 4

found in Table 11.1-4.

The heat exchangers are located in the RXB on the 50' elevation inside the heat exchanger rooms.

Module Heating System Heat Exchangers The module heating system heat exchangers are modeled with the tube side filled with design basis primary coolant. No credit was given for shielding provided by the tubes or the clean steam and water filling the shell side.

Resin Transfer Pipe A generic resin transfer line is modeled assuming it is 100 percent obstructed by spherical resin beads from the CVCS mixed bed demineralizer, which has been modeled using a bulk dry resin density. The generic resin transfer line is modeled with the parameters listed in Table 12.2-6. 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 12.2-7 and Table 12.2-8, with a spent resin volume of 8.8 ft3.

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 assumed to remove crud particulate. The assumed filter efficiency is listed in Table 12.2-6. The filter source term and source strengths are listed in Table 12.2-7 and Table 12.2-8, respectively.

2.1.4 Reactor Pool Cooling, Spent Fuel Pool Cooling and Pool Cleanup Systems The reactor pool cooling system (RPCS) is a cooling-water system that removes heat from the reactor pool, while the spent fuel pool cooling system (SFPCS) removes heat by drawing water from the spent fuel pool. The pool cleanup system (PCUS) draws water from either the SFPCS or the RPCS and removes impurities to reduce radiation exposures and to maintain water chemistry and clarity. These systems are further described in Section 9.1.3.

The RPCS and SFPCS 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 primary system components considered in designing shielding are the PCUS demineralizers and filters that accumulate activity from radioactive contamination in the reactor pool water. The PCUS demineralizers are assumed to collect the entire inventory of radioactivity in the pool water as reflected in Table 12.2-10. It is also assumed that the PCUS demineralizers operate for two years, resulting in the collection of the entire reactor pool water radionuclide inventory 12 times (assuming a plant with 12 NPMs on a 2 year refueling cycle).

2 12.2-3 Revision 4

The input assumptions used to develop these source terms are listed in Table 12.2-9.

The radionuclide source terms and source strengths for this equipment are provided in Table 12.2-10 and Table 12.2-11, respectively.

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. The radionuclide inventories are listed for the major LRWS components in Table 12.2-13a and Table 12.2-13b which are the basis for the liquid radioactive waste component shielding design.

The estimated input flows from various sources to the high-conductivity waste (HCW) collection tanks, and the low-conductivity waste (LCW) collection tanks are listed in Table 11.2-3. 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. The assumed values for the LRW processing equipment radionuclide collection efficiencies are listed in Table 12.2-12. The LRWS component source terms are provided in Table 12.2-13a and Table 12.2-13b, and source strengths are provided in Table 12.2-14a and Table 12.2-14b. To establish the shielding design downstream of the GAC filter, the radionuclide concentration in the outlet stream from the GAC filter is assumed to not be reduced by the GAC filter.

2.1.6 Gaseous Radioactive Waste System Radioactive fission gases are produced in the reactor core and assumed to be released to the primary coolant, as discussed in Section 11.1. 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 12.2-15 lists the assumed values pertaining to the GRWS source geometries and Table 11.3-1 describes the GRWS processing parameters. The GRWS component source terms are provided in Table 12.2-16 and the source strengths are provided in Table 12.2-17.

The radioisotopic inventory listed in Table 12.2-16 for the GRWS guard bed and decay beds results in a RG 1.143 safety classification of RW-IIb. Because an end of operating cycle degasification evolution could result in a transient radioisotopic inventory that exceeds that listed in Table 12.2-16, the RG 1.143 safety classifications for the GRWS guard bed and decay beds are increased from RW-IIb to RW-IIa to cover such transients, as reflected in Table 11.3-2.

2.1.7 Solid Radioactive Waste System The solid radioactive waste system (SRWS) handles solid radioactive waste from various waste streams, as described in Section 11.4. The waste inputs to the SRWS components are collected, resulting in a radionuclide source term for the SRWS components. The 2 12.2-4 Revision 4

components and Table 12.2-20 lists the SRWS component source strengths. As described in Section 11.4, there is storage space provided in the Radioactive Waste Building for processed waste packages that contain spent filters, dewatered resins, and other solid wastes. For shielding design purposes, it is assumed that the Class A/B/C high integrity container storage area contains five high integrity containers loaded with Class B/C dewatered spent resins from the spent resin storage tank, which has been decayed for approximately two years (one fuel cycle), and one 55-gallon drum filled with waste from the LRWS drum dryer. Table 12.2-13b provides the radionuclide inventory of the drum dryer and Table 12.2-14b 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 The reactor pool is housed within the RXB and contains up to 12 NPMs, which are partially immersed in the reactor pool water. Because the spent fuel pool communicates with the reactor pool through the weir wall, radionuclides are mixed with the spent fuel pool water volume. 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 small 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 will operate until the projected dose rate (after NPM disassembly) to an operator on the refueling bridge is less than 2.5 mR/hr.

The other major input assumptions for the pool water source term are provided in Table 12.2-9.

The radionuclide contribution resulting from neutron activation of the reactor pool water contents is not significant due to the reduced neutron flux in the reactor pool 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 quickly decrease in the reactor pools borated water. The small amount of neutron activation products in the reactor pool water was calculated to be insignificant compared to the amount of primary coolant radionuclides released to the reactor pool water during refueling outages. The reactor pool and RCS water chemistry limits (when the temperature of the RCS is less than 250 degrees F) are in conformance with the Electric Power Research Institute primary water chemistry guidelines (Reference 12.2-3). The reactor pool water volume dilutes inadvertently introduced impurities that could result from component failures and, because the chemistry limits in both the reactor pool and each NPM are monitored, impurities in either of the two water sources are minimized.

Between refueling outages, the radionuclides in the reactor pool water are treated by the PCUS demineralizers and filters to reduce the radionuclide content. The pool water 2 12.2-5 Revision 4

The pool surge control system (PSCS) storage tank is designed to temporarily store cleaned up pool water that is displaced during drydock operations. The PSCS storage tank is modeled as a vertical cylindrical tank with the characteristics listed in Table 12.2-9.

The source terms and the source strengths for the pool water and the PSCS storage tank are provided in Table 12.2-10 and Table 12.2-11, respectively.

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's concrete 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 freshly-discharged, 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 12.2-21 for a spent fuel rack full of freshly discharged fuel assemblies. Spent fuel neutron source strengths are given in Table 12.2-22 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. The major inputs assumptions are listed in Table 12.2-23. The gamma spectra are provided in Table 12.2-24.

2.1.11 Control Rods and Secondary Source Rods Control Rod Assemblies The control rod assemblies are irradiated during reactor operations. 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. The major input assumptions are listed in Table 12.2-25.

The CRA gamma spectra are listed in Table 12.2-26.

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

The gamma ray source strengths associated with the secondary source rods are listed in Table 12.2-27 for various times after shutdown.

2 12.2-6 Revision 4

The secondary coolant system is expected to contain minimal radioactivity during normal operations. Primary-to-secondary leaks through the steam generator can introduce primary coolant activity into the secondary system with the resultant contamination level being dependent upon 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 were 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 ten day resin regeneration period, the accumulation of radioactive material is less than 100 mCi.

2.1.13 Post-Accident Sources The iodine spike design basis source term (the maximum primary coolant activity released from design basis accidents described in Section 15.0.3) is evaluated for equipment qualification (EQ) in and around an NPM. Three volumes associated with the NPM are evaluated for EQ dose consequences: 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 equipment qualification evaluation are provided on a mass basis in Table 12.2-34. The specific concentration values in Table 12.2-34 are in excess of the values that would be calculated using the methodology in TR-0915-17565, Accident Source Term Methodology, Rev. 3, with the design inputs provided in this FSAR. 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 12.2-28. The three volumes are evaluated with conservative assumptions, including instantaneous and homogeneous releases into the volume of interest.

Table 12.2-31 lists the integrated post-accident source energy deposition versus time for both photons and electrons for the three evaluated volumes. Table 12.2-31 also tabulates the integrated doses for various times post-accident. For additional details on equipment qualification, see Section 3.11 and Appendix 3.C. Consistent with 10 CFR 50.34(f)(2)(vii), areas that could contain core damage post-accident sources were evaluated for equipment protection. Information on equipment protection from a core damage source term is addressed in Section 19.2.

2.1.14 Other Contained Sources There are no other identified contained sources that exceed 100 mCi, including HVAC filters. To evaluate the accumulation of radioactive material on the Reactor Building HVAC system HEPA filters, the airborne radioactivity in the Reactor Building due to pool evaporation and primary coolant leaks was deposited on filters assuming a 99 percent particulate efficiency and two years of operation. For the pool evaporation portion, the Reactor Building HVAC system provides a ventilation flow rate equivalent to one air volume change per hour. For the primary coolant leakage portion, the activity that 2 12.2-7 Revision 4

Item 12.2-1: A COL applicant that references the NuScale Power Plant design certification 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 RXB atmosphere due to reactor pool evaporation or primary coolant leakage. The airborne concentration is modeled as a buildup to an equilibrium concentration based on Bevelacqua (Reference 12.2-1) given the production rate and removal rate, and on an evaporation rate based on ASHRAE (Reference 12.2-6). 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 reactor coolant system. Each case maximizes the tritium concentration in the fluid of interest. These values are reported 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. The input parameters are listed in Table 12.2-32.

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),

where, A = area of pool surface, ft2 2 12.2-8 Revision 4

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.

The resultant airborne isotopic concentrations in the RXB atmosphere are listed in Table 12.2-33. Monitoring airborne radioactivity within the air spaces of the facility is described in Section 12.3.4. Monitoring gaseous effluents is described in Section 11.5.

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

2.3 References 12.2-1 Bevelacqua, J.J., Basic Health Physics, Problems and Solutions, Wiley-VCH Publishing, Weinheim, Germany, 2004.

2 12.2-9 Revision 4

February 2003.

12.2-3 Electric Power Research Institute, "Pressurized Water Reactor Primary Water Chemistry Guidelines," Vols. 1 and 2, EPRI #3002000505, Rev. 7, Palo Alto, CA, 2014.

12.2-4 Not Used.

12.2-5 Not Used.

12.2-6 American Society of Heating, Refrigerating and Air-Conditioning Engineers, 2007 ASHRAE Handbook Applications, Atlanta, GA.

2 12.2-10 Revision 4

Parameter Value on neutron source strength 1.91E+19 particles/sec on neutron energy spectrum Watt spectrum for U-235 on gamma source strength 1.45E+20 particles/sec Leg Fraction of Primary coolant 27%

Leg Fraction of Primary coolant 73%

l Primary Coolant source strength 1.06E+14 particles/sec 2 12.2-11 Revision 4

Energy Bin Boundaries Probability Density Function (eV) 0.00E+00 - 5.00E+04 1.417E-07 5.00E+04 - 1.00E+05 2.367E-07 1.00E+05 - 1.50E+05 3.954E-07 1.50E+05 - 1.63E+05 6.676E-07 1.63E+05 - 1.78E+05 7.101E-07 1.78E+05 - 2.00E+05 6.123E-07 2.00E+05 - 2.12E+05 8.632E-07 2.12E+05 - 2.25E+05 1.106E-06 2.25E+05 - 2.45E+05 8.433E-07 2.45E+05 - 2.65E+05 6.094E-07 2.65E+05 - 3.00E+05 4.110E-07 3.00E+05 - 3.25E+05 6.846E-07 3.25E+05 - 3.50E+05 8.178E-07 3.50E+05 - 3.65E+05 1.030E-06 3.65E+05 - 4.00E+05 1.066E-06 4.00E+05 - 4.30E+05 9.396E-07 4.30E+05 - 4.50E+05 8.418E-07 4.50E+05 - 4.85E+05 8.844E-07 4.85E+05 - 5.00E+05 9.964E-07 5.00E+05 - 5.25E+05 9.596E-07 5.25E+05 - 5.45E+05 8.249E-07 5.45E+05 - 5.75E+05 7.327E-07 5.75E+05 - 6.05E+05 8.759E-07 6.05E+05 - 6.25E+05 9.538E-07 6.25E+05 - 6.50E+05 8.632E-07 6.50E+05 - 6.70E+05 7.285E-07 6.70E+05 - 6.83E+05 7.753E-07 6.83E+05 - 7.00E+05 7.994E-07 7.00E+05 - 7.50E+05 7.186E-07 7.50E+05 - 8.00E+05 6.973E-07 8.00E+05 - 9.00E+05 6.633E-07 9.00E+05 - 1.00E+06 5.102E-07 1.00E+06 - 1.10E+06 4.209E-07 1.10E+06 - 1.20E+06 3.586E-07 1.20E+06 - 1.25E+06 3.415E-07 1.25E+06 - 1.35E+06 3.274E-07 1.35E+06 - 1.50E+06 2.821E-07 1.50E+06 - 1.75E+06 2.013E-07 1.75E+06 - 2.00E+06 1.289E-07 2.00E+06 - 2.25E+06 9.349E-08 2.25E+06 - 2.50E+06 7.367E-08 2.50E+06 - 2.75E+06 5.866E-08 2.75E+06 - 3.00E+06 4.504E-08 3.00E+06 - 3.25E+06 3.433E-08 3.25E+06 - 3.50E+06 2.482E-08 2 12.2-12 Revision 4

Energy Bin Boundaries Probability Density Function (eV) 3.50E+06 - 3.75E+06 1.972E-08 3.75E+06 - 4.00E+06 1.562E-08 4.00E+06 - 4.25E+06 1.271E-08 4.25E+06 - 4.50E+06 9.349E-09 4.50E+06 - 4.75E+06 6.577E-09 4.75E+06 - 5.00E+06 5.075E-09 5.00E+06 - 5.25E+06 4.214E-09 5.25E+06 - 5.50E+06 3.554E-09 5.50E+06 - 5.75E+06 3.023E-09 5.75E+06 - 6.00E+06 2.583E-09 6.00E+06 - 6.25E+06 2.172E-09 6.25E+06 - 6.50E+06 1.762E-09 6.50E+06 - 6.75E+06 1.421E-09 6.75E+06 - 7.00E+06 1.101E-09 7.00E+06 - 7.50E+06 8.609E-10 7.50E+06 - 7.75E+06 4.204E-10 7.75E+06 - 8.00E+06 1.201E-10 8.00E+06 - 8.10E+06 1.001E-11 2 12.2-13 Revision 4

Gamma Source Lower Bound Upper Bound (photons/sec/gram primary Energy Group (MeV) (MeV) coolant) 1 1.00E-02 2.00E-02 3.38E+04 2 2.00E-02 3.00E-02 2.50E+04 3 3.00E-02 4.50E-02 1.03E+05 4 4.50E-02 6.00E-02 1.26E+04 5 6.00E-02 7.00E-02 6.19E+03 6 7.00E-02 7.50E-02 2.69E+03 7 7.50E-02 1.00E-01 8.49E+04 8 1.00E-01 1.50E-01 1.32E+04 9 1.50E-01 2.00E-01 1.09E+04 10 2.00E-01 2.60E-01 1.30E+04 11 2.60E-01 3.00E-01 9.78E+03 12 3.00E-01 4.00E-01 9.74E+04 13 4.00E-01 4.50E-01 3.43E+03 14 4.50E-01 5.10E-01 3.59E+03 15 5.10E-01 5.12E-01 1.37E+03 16 5.12E-01 6.00E-01 4.21E+04 17 6.00E-01 7.00E-01 1.33E+04 18 7.00E-01 8.00E-01 6.31E+03 19 8.00E-01 9.00E-01 5.59E+03 20 9.00E-01 1.00E+00 1.61E+03 21 1.00E+00 1.20E+00 3.06E+03 22 1.20E+00 1.33E+00 1.11E+04 23 1.33E+00 1.44E+00 1.46E+03 24 1.44E+00 1.50E+00 3.57E+02 25 1.50E+00 1.57E+00 4.26E+02 26 1.57E+00 1.66E+00 4.35E+02 27 1.66E+00 1.80E+00 1.50E+03 28 1.80E+00 2.00E+00 1.28E+03 29 2.00E+00 2.15E+00 4.89E+02 30 2.15E+00 2.35E+00 3.02E+02 31 2.35E+00 2.50E+00 1.16E+03 32 2.50E+00 2.75E+00 5.03E+03 33 2.75E+00 3.00E+00 1.34E+03 34 3.00E+00 3.50E+00 3.30E+02 35 3.50E+00 4.00E+00 3.71E+02 36 4.00E+00 4.50E+00 1.34E+02 37 4.50E+00 5.00E+00 1.25E+02 38 5.00E+00 5.50E+00 1.11E+02 39 5.50E+00 6.00E+00 5.49E+01 40 6.00E+00 6.50E+00 3.62E+05 41 6.50E+00 7.00E+00 2.37E+02 42 7.00E+00 7.50E+00 2.65E+04 43 7.50E+00 8.00E+00 7.58E+00 44 8.00E+00 1.00E+01 4.23E+02 2 12.2-14 Revision 4

Gamma Source Lower Bound Upper Bound (photons/sec/gram primary Energy Group (MeV) (MeV) coolant) 45 1.00E+01 1.20E+01 1.08E-01 46 1.20E+01 1.40E+01 -

47 1.40E+01 2.00E+01 -

Total 9.08E+05

This source term is used for 73 percent by mass of the primary coolant in the NuScale operating reactor shielding ulation, for the pressurizer region above the pressurizer plate and from the steam generator to the cold inlet of the core.

2 12.2-15 Revision 4

Gamma Source Lower Bound Upper Bound (photons/sec/gram primary Energy Group (MeV) (MeV) coolant) 1 1.00E-02 2.00E-02 2.95E+05 2 2.00E-02 3.00E-02 1.77E+05 3 3.00E-02 4.50E-02 2.28E+05 4 4.50E-02 6.00E-02 1.12E+05 5 6.00E-02 7.00E-02 5.52E+04 6 7.00E-02 7.50E-02 2.41E+04 7 7.50E-02 1.00E-01 1.75E+05 8 1.00E-01 1.50E-01 1.14E+05 9 1.50E-01 2.00E-01 8.99E+04 10 2.00E-01 2.60E-01 6.06E+04 11 2.60E-01 3.00E-01 3.33E+04 12 3.00E-01 4.00E-01 1.61E+05 13 4.00E-01 4.50E-01 2.59E+04 14 4.50E-01 5.10E-01 2.80E+04 15 5.10E-01 5.12E-01 1.37E+03 16 5.12E-01 6.00E-01 5.44E+04 17 6.00E-01 7.00E-01 3.32E+04 18 7.00E-01 8.00E-01 2.17E+04 19 8.00E-01 9.00E-01 1.78E+04 20 9.00E-01 1.00E+00 1.17E+04 21 1.00E+00 1.20E+00 1.80E+04 22 1.20E+00 1.33E+00 1.95E+04 23 1.33E+00 1.44E+00 6.06E+03 24 1.44E+00 1.50E+00 2.36E+03 25 1.50E+00 1.57E+00 2.35E+03 26 1.57E+00 1.66E+00 3.82E+03 27 1.66E+00 1.80E+00 1.14E+04 28 1.80E+00 2.00E+00 9.30E+03 29 2.00E+00 2.15E+00 2.94E+03 30 2.15E+00 2.35E+00 3.02E+02 31 2.35E+00 2.50E+00 7.19E+03 32 2.50E+00 2.75E+00 4.43E+04 33 2.75E+00 3.00E+00 1.11E+04 34 3.00E+00 3.50E+00 2.97E+03 35 3.50E+00 4.00E+00 3.42E+03 36 4.00E+00 4.50E+00 1.24E+03 37 4.50E+00 5.00E+00 1.15E+03 38 5.00E+00 5.50E+00 1.04E+03 39 5.50E+00 6.00E+00 5.12E+02 40 6.00E+00 6.50E+00 3.38E+06 41 6.50E+00 7.00E+00 2.21E+03 42 7.00E+00 7.50E+00 2.47E+05 43 7.50E+00 8.00E+00 7.07E+01 44 8.00E+00 1.00E+01 3.94E+03 2 12.2-16 Revision 4

Gamma Source Lower Bound Upper Bound (photons/sec/gram primary Energy Group (MeV) (MeV) coolant) 45 1.00E+01 1.20E+01 1.01E+00 46 1.20E+01 1.40E+01 -

47 1.40E+01 2.00E+01 -

Total 5.50E+06

This source term is used for 27 percent by mass of the primary coolant in the NuScale operating reactor shielding ulation, for primary coolant leaving the core to the top of the upper riser.

2 12.2-17 Revision 4

Primary Coolant Location N-16 concentration (Ci/gram) exit 139 of upper riser / entrance to SG 14.9 S letdown line 1.80 2 12.2-18 Revision 4

Assumptions Model Parameter Value S mixed bed:

VCS mixed bed operation time 100% of fuel cycle econtamination Factors Table 11.1-2 eometry vertical cylinder Source dimensions of vessel diameter=24; height=96 Shielding thickness of steel shell 1.5 Volume of resin 8.8 ft3 S Cation bed:

VCS Cation Bed Operation Time 50% of fuel cycle VCS Cation Bed Decontamination Factors:

Halogens 1 Cs, Rb 10 Others 10 eometry vertical cylinder Source dimensions of vessel diameter=24; height=96 Shielding thickness of steel shell 1.5 nerative and Non-Regenerative Heat Exchangers:

ontents 100% primary coolant (see Table 11.1-4) eometry vertical stack of 5 horizontal cylinders Source dimensions of each cylinder diameter=12; length=11.5 Shielding thickness of steel shell Regenerative heat exchanger 1" Non-Regenerative heat exchanger 0.406" ule Heating System Heat Exchangers ontents 100% primary coolant (see Table 11.1-4) eometry horizontal cylinder Source dimensions diameter=21.5; length=13.1 Shielding thickness of steel shell 1.25 S flowrate 22 gpm S filter efficiency 9.1% (DF = 1.1) eometry vertical cylinder Dimensions diameter=13; height=48 Shielding thickness of steel shell 0.5 S resin transfer line:

pe internal diameter 2" pe wall thickness 0.154" pe length 20 pe material Stainless steel esin source term CVCS mixed bed resin (48-hr decay)

S pipe inside vertical pipe chase ontents Primary coolant (see Table 12.2-8) eometry vertical cylinder Source length of pipe 20 Shielding dimensions of pipe inside diameter=2.5; thickness=0.375 2 12.2-19 Revision 4

Radionuclide Content CVCS Mixed Bed Transfer hour CVCS Mixed Bed CVCS Cation Bed CVCS Particulate Filter decay Isotope Ci Ci Ci Ci Br82 3.40E-02 - - 1.33E-02 Br83 1.32E-02 - - 1.26E-08 Br84 1.36E-03 - - 7.42E-31 Br85 1.50E-05 - - -

I129 2.82E-04 8.69E-11 - 2.82E-04 I130 9.62E-02 - - 6.52E-03 I131 3.74E+01 5.99E-04 - 3.15E+01 I132 1.76E+00 1.43E-02 - 1.04E+00 I133 4.62E+00 1.20E-05 - 9.33E-01 I134 4.87E-02 1.57E-05 - 1.70E-18 I135 1.25E+00 - - 7.88E-03 Rb86m 1.97E-09 8.85E-10 - -

Rb86 3.08E-01 1.39E-01 - 2.86E-01 Rb88 3.48E-02 1.57E-02 - 6.03E-51 Rb89 1.36E-03 6.12E-04 - 8.10E-61 Cs132 2.06E-03 9.29E-04 - 1.67E-03 Cs134 1.03E+03 2.70E+02 - 1.03E+03 Cs135m 7.95E-05 3.58E-05 - 3.49E-21 Cs136 7.96E+00 3.58E+00 - 7.16E+00 Cs137 8.43E+02 1.92E+02 - 8.43E+02 Cs138 2.40E-02 1.08E-02 - 2.70E-28 P32 1.32E-06 1.21E-08 - 1.20E-06 Co57 1.57E-07 1.03E-09 - 1.56E-07 Sr89 2.10E-01 2.51E-03 - 2.04E-01 Sr90 4.47E-01 2.08E-03 - 4.47E-01 Sr91 8.61E-04 7.90E-06 - 2.72E-05 Sr92 1.27E-04 1.17E-06 - 4.70E-10 Y90 4.45E-01 2.06E-03 - 4.46E-01 Y91m 5.41E-04 4.97E-06 - 1.73E-05 Y91 3.55E-02 3.21E-04 - 3.46E-02 Y92 2.71E-04 2.49E-06 - 5.28E-08 Y93 1.94E-04 1.78E-06 - 7.39E-06 Zr97 4.70E-04 4.32E-06 - 6.44E-05 Nb95 7.27E-01 6.39E-03 - 7.25E-01 Mo99 3.32E+00 3.05E-02 - 2.01E+00 Mo101 4.63E-04 4.25E-06 - 2.11E-63 Tc99m 3.20E+00 2.94E-02 - 1.94E+00 Tc99 1.71E-02 7.84E-05 - 1.71E-02 Ru103 4.54E-02 4.16E-04 - 4.38E-02 Ru105 7.03E-05 6.46E-07 - 3.91E-08 Ru106 2.05E-01 1.24E-03 - 2.05E-01 Rh103m 4.49E-02 4.12E-04 - 4.33E-02 2 12.2-20 Revision 4

CVCS Mixed Bed Transfer hour CVCS Mixed Bed CVCS Cation Bed CVCS Particulate Filter decay Isotope Ci Ci Ci Ci Rh105 1.26E-03 1.16E-05 - 4.96E-04 Rh106 2.05E-01 1.24E-03 - 2.05E-01 Ag110 1.07E-01 7.14E-04 - 1.06E-01 Sb124 1.03E-04 9.27E-07 - 1.00E-04 Sb125 5.86E-03 3.02E-05 - 5.85E-03 Sb127 2.51E-04 2.30E-06 - 1.75E-04 Sb129 1.47E-05 1.35E-07 - 7.63E-09 Te125m 1.28E-01 1.15E-03 - 1.25E-01 Te127m 7.66E-01 6.37E-03 - 7.56E-01 Te127 7.58E-01 6.32E-03 - 7.41E-01 Te129m 6.84E-01 6.28E-03 - 6.56E-01 Te129 4.32E-01 3.97E-03 - 4.14E-01 Te131m 8.32E-02 7.64E-04 - 2.74E-02 Te131 1.90E-02 1.75E-04 - 6.18E-03 Te132 1.55E+00 1.43E-02 - 1.01E+00 Te133m 1.59E-03 1.46E-05 - 3.56E-19 Te134 1.71E-03 1.57E-05 - 3.10E-24 Ba137m 7.96E+02 1.81E+02 - 7.96E+02 Ba139 6.31E-05 5.79E-07 - 2.30E-15 Ba140 7.60E-02 6.98E-04 - 6.82E-02 La140 7.90E-02 7.25E-04 - 7.48E-02 La141 5.54E-05 5.09E-07 - 1.14E-08 La142 1.03E-05 9.41E-08 - 3.12E-15 Ce141 2.99E-02 2.75E-04 - 2.87E-02 Ce143 9.57E-04 8.79E-06 - 3.50E-04 Ce144 1.81E-01 1.17E-03 - 1.80E-01 Pr143 1.21E-02 1.11E-04 - 1.09E-02 Pr144 1.79E-01 1.16E-03 - 1.78E-01 Np239 3.44E-02 3.16E-04 - 1.91E-02 Na24 6.17E-01 8.77E-03 1.77E-03 6.67E-02 Cr51 2.39E+00 2.22E-02 4.48E-03 2.28E+00 Mn54 1.11E+01 7.03E-02 1.42E-02 1.11E+01 Fe55 1.31E+01 6.75E-02 1.36E-02 1.31E+01 Fe59 3.72E-01 3.43E-03 6.92E-04 3.61E-01 Co58 9.10E+00 8.14E-02 1.65E-02 8.93E+00 Co60 6.46E+00 3.16E-02 6.37E-03 6.45E+00 Ni63 3.63E+00 1.67E-02 3.38E-03 3.63E+00 Zn65 3.02E+00 2.04E-02 4.11E-03 3.00E+00 Zr95 6.97E-01 6.30E-03 1.27E-03 6.82E-01 Ag110m 7.84E+00 5.25E-02 1.06E-02 7.79E+00 W187 5.87E-02 7.09E-04 1.43E-04 1.44E-02 2 12.2-21 Revision 4

Source Strengths rgy Energy Boundary Design Basis CVCS Mixed CVCS Cation CVCS CVCS Mixed up (MeV) Primary Coolant Bed Bed Particulate Bed Transfer -

Photon Spectra (photon/s) (photon/s) Filter 48-hour decay (photon/s/gram) (photon/s) (photon/s) 1.00E-02 - 2.00E-02 2.09E+03 2.15E+11 4.69E+10 2.81E+06 2.06E+11 2.00E-02 - 3.00E-02 3.26E+03 2.27E+11 2.49E+10 5.68E+06 2.00E+11 3.00E-02 - 4.50E-02 8.54E+04 2.38E+12 5.25E+11 1.07E+06 2.36E+12 4.50E-02 - 6.00E-02 5.80E+02 6.18E+10 1.25E+10 1.03E+06 5.79E+10 6.00E-02 - 7.00E-02 2.79E+02 3.90E+10 1.21E+10 1.56E+06 3.68E+10 7.00E-02 - 7.50E-02 1.14E+02 1.03E+10 2.33E+09 9.24E+05 9.91E+09 7.50E-02 - 1.00E-01 7.16E+04 1.64E+11 1.51E+10 5.85E+05 1.45E+11 1.00E-01 - 1.50E-01 1.06E+03 1.63E+11 8.69E+09 1.87E+06 1.11E+11 1.50E-01 - 2.00E-01 1.19E+03 7.61E+10 2.47E+10 1.23E+06 6.66E+10 0 2.00E-01 - 2.60E-01 7.24E+03 1.09E+11 4.97E+09 7.87E+05 5.47E+10 1 2.60E-01 - 3.00E-01 2.69E+02 1.26E+11 1.51E+10 2.40E+05 1.06E+11 2 3.00E-01 - 4.00E-01 1.37E+03 1.33E+12 5.75E+10 1.61E+07 1.12E+12 3 4.00E-01 - 4.50E-01 4.71E+02 1.89E+10 2.28E+08 1.50E+07 1.37E+10 4 4.50E-01 - 5.10E-01 2.95E+02 5.76E+11 1.48E+11 1.58E+06 5.72E+11 5 5.10E-01 - 5.12E-01 5.37E+02 1.08E+11 9.29E+08 1.85E+08 1.04E+11 6 5.12E-01 - 6.00E-01 2.61E+03 9.38E+12 2.42E+12 5.09E+05 9.25E+12 7 6.00E-01 - 7.00E-01 2.84E+03 6.21E+13 1.52E+13 4.58E+08 6.20E+13 8 7.00E-01 - 8.00E-01 1.82E+03 3.66E+13 9.52E+12 2.16E+08 3.66E+13 9 8.00E-01 - 9.00E-01 1.37E+03 2.80E+12 5.30E+11 1.42E+09 2.75E+12 0 9.00E-01 - 1.00E+00 3.01E+02 1.14E+11 8.14E+08 1.33E+08 1.06E+11 1 1.00E+00 - 1.20E+00 9.71E+02 1.62E+12 3.72E+11 3.44E+08 1.58E+12 2 1.20E+00 - 1.33E+00 8.27E+03 2.14E+11 2.67E+10 1.36E+08 1.87E+11 3 1.33E+00 - 1.44E+00 8.41E+02 1.35E+12 2.99E+11 2.76E+08 1.33E+12 4 1.44E+00 - 1.50E+00 1.19E+02 1.76E+10 9.46E+07 1.64E+07 1.28E+10 5 1.50E+00 - 1.57E+00 1.98E+02 4.39E+10 4.39E+08 5.73E+07 4.24E+10 6 1.57E+00 - 1.66E+00 3.23E+01 3.05E+09 2.76E+07 9.52E+04 2.74E+09 7 1.66E+00 - 1.80E+00 3.20E+02 1.21E+10 2.28E+07 3.10E+06 2.02E+09 8 1.80E+00 - 2.00E+00 3.29E+02 2.21E+09 1.40E+08 6.65E+04 8.22E+08 9 2.00E+00 - 2.15E+00 1.97E+02 1.02E+09 1.01E+07 3.93E+03 3.29E+08 0 2.15E+00 - 2.35E+00 3.02E+02 7.67E+08 6.64E+07 2.71E+03 2.09E+08 1 2.35E+00 - 2.50E+00 4.47E+02 6.34E+08 2.16E+06 2.91E+00 9.77E+07 2 2.50E+00 - 2.75E+00 3.67E+02 1.22E+10 2.21E+08 3.43E+07 1.41E+09 3 2.75E+00 - 3.00E+00 1.82E+02 1.09E+10 1.56E+08 3.13E+07 1.18E+09 4 3.00E+00 - 3.50E+00 1.65E+01 1.56E+07 4.82E+06 6.00E-02 8.98E+05 5 3.50E+00 - 4.00E+00 8.39E+00 2.28E+07 1.04E+06 5.00E+04 1.88E+06 6 4.00E+00 - 4.50E+00 2.09E+00 7.21E+05 1.80E+05 5.49E+02 2.07E+04 7 4.50E+00 - 5.00E+00 3.75E+00 2.45E+06 1.10E+06 - -

8 5.00E+00 - 5.50E+00 1.28E+00 4.62E+03 2.07E+03 - -

9 5.50E+00 - 6.00E+00 6.30E-01 - - - -

0 6.00E+00 - 6.50E+00 4.16E+03 - - - -

1 6.50E+00 - 7.00E+00 2.72E+00 - - - -

2 7.00E+00 - 7.50E+00 3.04E+02 - - - -

3 7.50E+00 - 8.00E+00 8.70E-02 - - - -

2 12.2-22 Revision 4

rgy Energy Boundary Design Basis CVCS Mixed CVCS Cation CVCS CVCS Mixed up (MeV) Primary Coolant Bed Bed Particulate Bed Transfer -

Photon Spectra (photon/s) (photon/s) Filter 48-hour decay (photon/s/gram) (photon/s) (photon/s) 4 8.00E+00 - 1.00E+01 4.85E+00 - - - -

5 1.00E+01 - 1.20E+01 1.24E-03 - - - -

6 1.20E+01 - 1.40E+01 - - - - -

7 1.40E+01 - 2.00E+01 - - - - -

al 2.02E+05 1.20E+14 2.93E+13 3.36E+09 1.19E+14 2 12.2-23 Revision 4

Surge Control System Component Source Term Inputs and Assumptions Model Parameter Value tor pool cooling heat exchanger:

ontents 100% pool water ource term mass 3.88E+06 grams eometry horizontal cylinder Source dimensions diameter=2-8; height=24-7 Shielding thickness of steel shell 1/4 t fuel pool cooling heat exchanger:

ontents 100% pool water ource term mass 3.88E+06 grams eometry horizontal cylinder Source dimensions diameter=2-8; height=24-7 Shielding thickness of steel shell 1/4 cleanup system demineralizer:

eometry vertical cylinder Source dimensions diameter=13; height=5 Shielding thickness of steel shell 1/2 peration time 2 years (12 refuelings) filters:

CU filter efficiency 9.1%

eometry vertical cylinder Source dimensions diameter=2; height=9-8 Shielding thickness of steel shell 1/2 CU filter operation time 1 year (6 refuelings)

Surge Tank ontents cleaned up pool water eometry vertical cylinder Source dimensions diameter=61; height=50 Shielding thickness of steel wall 1/4 ource volume 1.46E+05 ft3 ce Mass 4.14E+09 grams

Assumes the plant consists of 12 NPMs operating on a two-year refueling cycle.

2 12.2-24 Revision 4

Control System Component Source Terms - Radionuclide Content Isotope RPCS Heat Spent Fuel Pool PCUS Reactor Pool PSC Surge Tank PCU Filter (Ci)

Exchanger (Ci) Cooling Heat Demineralizer Water (Ci/g) (Ci/g)

Exchanger (Ci) (Ci)

Br82 9.09E-08 9.09E-08 2.34E-05 2.34E-14 2.34E-16 -

Br83 2.86E-12 2.86E-12 5.00E-11 7.36E-19 - -

Br84 - - - - - -

Br85 - - - - - -

I129 5.44E-12 5.44E-12 4.82E-07 1.40E-18 1.40E-20 -

I130 1.42E-07 1.42E-07 1.28E-05 3.67E-14 3.67E-16 -

I131 3.89E-03 3.89E-03 5.46E+00 1.00E-09 1.00E-11 -

I132 3.24E-06 3.24E-06 1.82E-03 8.36E-13 8.36E-15 -

I133 4.61E-04 4.61E-04 6.99E-02 1.19E-10 1.19E-12 -

I134 - - 3.05E-20 - - -

I135 3.76E-07 3.76E-07 1.80E-05 9.69E-14 9.69E-16 -

Rb86m - - - - - -

Rb86 5.71E-07 5.71E-07 1.80E-03 1.47E-13 7.35E-14 -

Rb88 - - - - - -

Rb89 - - - - - -

Cs132 9.64E-09 9.64E-09 1.06E-05 2.48E-15 1.24E-15 -

Cs134 1.05E-04 1.05E-04 6.59E+00 2.72E-11 1.36E-11 -

Cs135m - - - - - -

Cs136 2.03E-05 2.03E-05 4.52E-02 5.22E-12 2.61E-12 -

Cs137 6.47E-05 6.47E-05 5.43E+00 1.67E-11 8.33E-12 -

Cs138 - - - - - -

P32 8.23E-13 8.23E-13 2.05E-09 2.12E-19 - -

Co57 6.69E-15 6.69E-15 2.69E-10 - - -

Sr89 3.97E-08 3.97E-08 3.51E-04 1.02E-14 2.05E-16 -

Sr90 9.04E-09 9.04E-09 7.82E-04 2.33E-15 4.66E-17 -

Sr91 8.19E-10 8.19E-10 5.75E-08 2.11E-16 4.22E-18 -

Sr92 9.02E-14 9.02E-14 1.75E-12 2.33E-20 - -

Y90 4.83E-09 4.83E-09 7.80E-04 1.25E-15 2.49E-17 -

Y91m 5.22E-10 5.22E-10 3.67E-08 1.35E-16 2.69E-18 -

Y91 5.77E-09 5.77E-09 5.91E-05 1.49E-15 2.98E-17 -

Y92 6.17E-12 6.17E-12 1.61E-10 1.59E-18 3.18E-20 -

Y93 2.08E-10 2.08E-10 1.54E-08 5.36E-17 1.07E-18 -

Zr97 1.02E-09 1.02E-09 1.24E-07 2.63E-16 5.25E-18 -

Nb95 3.81E-06 3.81E-06 1.06E+00 9.83E-13 1.97E-14 -

Mo99 7.34E-06 7.34E-06 3.53E-03 1.89E-12 3.78E-14 -

Mo101 - - - - - -

Tc99m 7.08E-06 7.08E-06 3.41E-03 1.83E-12 3.65E-14 -

Tc99 3.37E-10 3.37E-10 2.99E-05 8.69E-17 1.74E-18 -

Ru103 1.09E-08 1.09E-08 7.49E-05 2.81E-15 5.62E-17 -

Ru105 3.29E-12 3.29E-12 1.07E-10 8.48E-19 1.70E-20 -

Ru106 7.28E-09 7.28E-09 3.53E-04 1.88E-15 3.75E-17 -

Rh103m 1.08E-08 1.08E-08 7.40E-05 2.78E-15 5.55E-17 -

Rh105 3.48E-09 3.48E-09 8.97E-07 8.96E-16 1.79E-17 -

2 12.2-25 Revision 4

Isotope RPCS Heat Spent Fuel Pool PCUS Reactor Pool PSC Surge Tank PCU Filter (Ci)

Exchanger (Ci) Cooling Heat Demineralizer Water (Ci/g) (Ci/g)

Exchanger (Ci) (Ci)

Rh106 7.28E-09 7.28E-09 3.53E-04 1.88E-15 3.75E-17 -

Ag110 4.81E-06 4.81E-06 1.64E-01 1.24E-12 2.48E-14 -

Sb124 1.63E-11 1.63E-11 1.71E-07 4.19E-18 8.38E-20 -

Sb125 1.46E-10 1.46E-10 1.02E-05 3.77E-17 7.53E-19 -

Sb127 4.52E-10 4.52E-10 3.05E-07 1.17E-16 2.33E-18 -

Sb129 6.50E-13 6.50E-13 2.09E-11 1.68E-19 - -

Te125m 2.10E-08 2.10E-08 2.13E-04 5.41E-15 1.08E-16 -

Te127m 6.83E-08 6.83E-08 1.29E-03 1.76E-14 3.52E-16 -

Te127 7.47E-08 7.47E-08 1.27E-03 1.93E-14 3.85E-16 -

Te129m 1.91E-07 1.91E-07 1.12E-03 4.92E-14 9.83E-16 -

Te129 1.20E-07 1.20E-07 7.08E-04 3.10E-14 6.20E-16 -

Te131m 2.29E-07 2.29E-07 5.01E-05 5.91E-14 1.18E-15 -

Te131 5.16E-08 5.16E-08 1.13E-05 1.33E-14 2.66E-16 -

Te132 3.15E-06 3.15E-06 1.76E-03 8.11E-13 1.62E-14 -

Te133m - - - - - -

Te134 - - - - - -

Ba137m 6.11E-05 6.11E-05 5.12E+00 1.57E-11 3.15E-13 -

Ba139 1.75E-18 1.75E-18 1.76E-17 - - -

Ba140 5.25E-08 5.25E-08 1.17E-04 1.35E-14 2.70E-16 -

La140 3.73E-08 3.73E-08 1.28E-04 9.62E-15 1.93E-16 -

La141 1.16E-12 1.16E-12 3.31E-11 2.98E-19 - -

La142 1.89E-18 1.89E-18 2.09E-17 - - -

Ce141 8.61E-09 8.61E-09 4.90E-05 2.22E-15 4.44E-17 -

Ce143 2.64E-09 2.64E-09 6.35E-07 6.79E-16 1.36E-17 -

Ce144 7.48E-09 7.48E-09 3.10E-04 1.93E-15 3.86E-17 -

Pr143 7.63E-09 7.63E-09 1.88E-05 1.97E-15 3.93E-17 -

Pr144 7.41E-09 7.41E-09 3.07E-04 1.91E-15 3.82E-17 -

Np239 8.19E-08 8.19E-08 3.38E-05 2.11E-14 4.22E-16 -

Na24 1.85E-06 1.85E-06 1.82E-04 4.78E-13 9.56E-15 2.05E-05 Cr51 8.11E-04 8.11E-04 3.53E+00 2.09E-10 4.18E-12 3.98E-01 Mn54 4.35E-04 4.35E-04 1.72E+01 1.12E-10 2.24E-12 1.34E+00 Fe55 3.27E-04 3.27E-04 2.04E+01 8.43E-11 1.69E-12 1.30E+00 Fe59 7.97E-05 7.97E-05 5.58E-01 2.05E-11 4.11E-13 6.26E-02 Co58 1.23E-02 1.23E-02 1.38E+02 3.18E-09 6.36E-11 1.51E+01 Co60 1.45E-04 1.45E-04 1.01E+01 3.72E-11 7.45E-13 6.08E-01 Ni63 7.22E-05 7.22E-05 5.71E+00 1.86E-11 3.72E-13 3.23E-01 Zn65 1.38E-04 1.38E-04 4.65E+00 3.57E-11 7.14E-13 3.87E-01 Zr95 1.04E-04 1.04E-04 1.05E+00 2.69E-11 5.38E-13 1.16E-01 Ag110m 3.53E-04 3.53E-04 1.21E+01 9.11E-11 1.82E-12 9.97E-01 W187 2.04E-04 2.04E-04 3.18E-02 5.27E-11 1.05E-12 3.58E-03 H3 3.25E-01 3.25E-01 - 8.37E-08 8.37E-08 -

C14 1.41E-06 1.41E-06 - 3.63E-13 3.63E-13 -

Assumes the plant consists of 12 NPMs operating on a two-year refueling cycle.

2 12.2-26 Revision 4

Surge Control System Component Source Terms - Source Strengths PCUS Reactor Pool Energy Boundary Demineralizer Water PSC Surge Tank PCU Filter ergy Group (MeV) (photon/s) (photon/s) (photon/s/g) (photon/s) 1 1.00E 2.00E-02 1.23E+10 1.26E+10 1.20E-02 1.08E+09 2 2.00E 3.00E-02 1.88E+10 4.14E+10 1.75E-02 9.93E+08 3 3.00E 4.50E-02 2.42E+10 2.56E+10 2.12E-02 4.65E+08 4 4.50E 6.00E-02 3.84E+09 6.15E+09 4.48E-03 3.54E+08 5 6.00E 7.00E-02 2.13E+09 1.45E+10 1.47E-02 1.95E+08 6 7.00E 7.50E-02 9.30E+08 8.81E+09 6.16E-03 9.01E+07 7 7.50E 1.00E-01 8.77E+09 2.83E+10 1.57E-02 2.80E+08 8 1.00E 1.50E-01 3.93E+09 1.13E+10 8.13E-03 3.65E+08 9 1.50E 2.00E-01 3.50E+09 6.27E+09 1.81E-02 2.70E+08 10 2.00E 2.60E-01 1.84E+09 2.05E+09 1.62E-03 1.58E+08 11 2.60E 3.00E-01 1.35E+10 6.82E+10 3.42E-02 6.28E+07 12 3.00E 4.00E-01 1.87E+11 9.29E+11 3.70E-01 1.52E+09 13 4.00E 4.50E-01 1.75E+10 5.11E+09 3.14E-03 1.44E+09 14 4.50E 5.10E-01 5.07E+09 1.97E+10 2.04E-02 7.38E+07 15 5.10E 5.12E-01 1.52E+12 1.01E+12 7.03E-01 1.67E+11 16 5.12E 6.00E-01 6.15E+10 1.16E+11 1.61E-01 3.28E+07 17 6.00E 7.00E-01 9.30E+11 2.58E+11 5.91E-01 4.29E+10 18 7.00E 8.00E-01 5.08E+11 1.23E+11 5.39E-01 2.02E+10 19 8.00E 9.00E-01 5.85E+12 3.44E+12 2.49E+00 6.13E+11 20 9.00E 1.00E+00 1.52E+11 3.33E+10 2.30E-02 1.25E+10 21 1.00E+00 - 1.20E+00 5.06E+11 7.94E+10 1.30E-01 3.27E+10 22 1.20E+00 - 1.33E+00 2.07E+11 3.66E+10 4.19E-02 1.29E+10 23 1.33E+00 - 1.44E+00 2.99E+11 4.49E+10 4.55E-02 2.01E+10 24 1.44E+00 - 1.50E+00 1.88E+10 4.08E+09 2.84E-03 1.55E+09 25 1.50E+00 - 1.57E+00 6.54E+10 1.41E+10 9.94E-03 5.39E+09 26 1.57E+00 - 1.66E+00 1.14E+08 3.88E+07 2.53E-05 8.95E+06 27 1.66E+00 - 1.80E+00 2.55E+10 1.70E+10 1.18E-02 2.80E+09 28 1.80E+00 - 2.00E+00 7.77E+07 3.60E+07 1.89E-05 6.26E+06 29 2.00E+00 - 2.15E+00 5.25E+06 9.72E+06 3.94E-06 3.70E+05 30 2.15E+00 - 2.35E+00 4.66E+06 4.82E+06 2.01E-06 2.59E+05 31 2.35E+00 - 2.50E+00 2.66E+05 2.93E+06 1.04E-06 2.32E+02 32 2.50E+00 - 2.75E+00 3.73E+06 2.66E+08 1.85E-04 3.97E+05 33 2.75E+00 - 3.00E+00 3.23E+06 2.42E+08 1.69E-04 3.63E+05 34 3.00E+00 - 3.50E+00 1.54E+03 2.86E+03 1.99E-09 6.95E-04 35 3.50E+00 - 4.00E+00 5.14E+03 3.87E+05 2.70E-07 5.79E+02 36 4.00E+00 - 4.50E+00 5.64E+01 4.25E+03 2.96E-09 6.35E+00 37 4.50E+00 - 5.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 38 5.00E+00 - 5.50E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 39 5.50E+00 - 6.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 40 6.00E+00 - 6.50E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 41 6.50E+00 - 7.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 42 7.00E+00 - 7.50E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 43 7.50E+00 - 8.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 2 12.2-27 Revision 4

PCUS Reactor Pool Energy Boundary Demineralizer Water PSC Surge Tank PCU Filter ergy Group (MeV) (photon/s) (photon/s) (photon/s/g) (photon/s) 44 8.00E+00 - 1.00E+01 0.00E+00 0.00E+00 0.00E+00 0.00E+00 45 1.00E+01 - 1.20E+01 0.00E+00 0.00E+00 0.00E+00 0.00E+00 46 1.20E+01 - 1.40E+01 0.00E+00 0.00E+00 0.00E+00 0.00E+00 47 1.40E+01 - 2.00E+01 0.00E+00 0.00E+00 0.00E+00 0.00E+00 Total 1.04E+13 6.35E+12 5.30E+00 9.38E+11

Assumes the plant consists of 12 NPMs operating on a two-year refueling cycle.

2 12.2-28 Revision 4

Assumptions Model Parameter Value S degasifier ontents CVCS letdown (see Table 11.2-11) eometry vertical cylinder Source dimensions diameter=12; height=14 Shield thickness of steel shell 1 olume 12,500 gallons and HCW collection tanks puts Table 11.2-3 eometry vertical cylinder Source dimensions diameter=12; height=15.13 Shield thickness of steel shell 0.25 olume 12,800 gallons S oil separator puts Table 11.2-3 eometry parallelepiped Source dimensions length=3; width=10; height=4 Shield thickness of steel shell 0.25 and HCW granulated activated charcoal (GAC) units econtamination Factors (from Reference 12.2-2)

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=3; height=6 Shield thickness of steel shell (Table 12.3-7) and HCW tubular ultrafiltration (TUF) units econtamination factors All nuclides 2.5 eometry vertical cylinder Source dimensions diameter=39; height=47.5 Shield thickness of steel shell (Table 12.3-7) and HCW reverse osmosis (RO) units econtamination factors All nuclides 10 eometry vertical cylinder Source dimensions diameter=39; height=47.5 Shield thickness of steel shell (Table 12.3-7) 2 12.2-29 Revision 4

Model Parameter Value cation bed econtamination factors Anions 1 Cs, Rb 10 Others 10 eometry vertical cylinder Source dimensions of vessel diameter=2.78; height=2.9 Shield thickness of steel shell (Table 12.3-7) anion bed econtamination factors Anions 100 Cs, Rb 1 Others 1 eometry vertical cylinder Source dimensions of vessel diameter=2.78; height=2.9 Shield thickness of steel shell (Table 12.3-7) cesium bed econtamination factors Anions 1 Cs, Rb 10 Others 10 eometry vertical cylinder Source dimensions of vessel diameter=2.78; height=2.9 Shield thickness of steel shell (Table 12.3-7) mixed bed econtamination Factors Anion 100 Cs, Rb 2 Others 100 eometry vertical cylinder Source dimensions of vessel diameter=4.46; height=1.68 Shield thickness of steel shell (Table 12.3-7) and HCW sample tanks eometry vertical cylinder Source dimensions diameter=12; height=15.13 Shield thickness of steel shell (Table 12.3-7) m dryer puts TUF and RO rejects eometry vertical cylinder Source dimensions diameter=18; height=28

Assumes the plant consists of 12 NPMs operating on a two-year refueling cycle.

2 12.2-30 Revision 4

Radionuclide Content otope LCW HCW Oil LCW GAC LCW TUF LCW RO LCW Cation LCW Anion Collection Collection Separator Unit Unit Unit Bed Bed Tank Tank (Ci) (Ci) (Ci) (Ci) (Ci) (Ci)

(Ci) (Ci)

Br82 2.95E-05 1.22E-04 7.54E-06 - 4.71E-06 2.83E-06 - 3.19E-07 Br83 1.66E-04 6.97E-04 4.31E-05 - 1.85E-06 1.11E-06 - 1.22E-07 Br84 7.73E-05 3.24E-04 2.01E-05 - 1.90E-07 1.14E-07 - 1.25E-08 Br85 9.34E-06 3.92E-05 2.42E-06 - 2.09E-09 1.26E-09 - 1.38E-10 I129 7.48E-10 3.02E-09 1.87E-10 - 4.49E-10 2.69E-10 2.32E-13 1.39E-09 I130 2.35E-04 9.84E-04 6.09E-05 - 1.35E-05 8.09E-06 - 8.90E-07 I131 2.67E-02 2.75E-02 1.57E-03 - 1.17E-02 7.00E-03 1.54E-06 1.57E-03 I132 2.77E-03 1.15E-02 7.14E-04 - 5.25E-04 3.15E-04 3.68E-05 1.94E-06 I133 1.15E-02 3.84E-02 2.36E-03 - 1.11E-03 6.67E-04 3.07E-08 7.34E-05 I134 1.62E-03 6.78E-03 4.20E-04 - 7.23E-06 4.34E-06 4.00E-08 4.33E-07 I135 5.72E-03 2.40E-02 1.49E-03 - 1.74E-04 1.05E-04 - 1.15E-05 b86m 4.03E-07 6.40E-08 1.76E-09 - 3.17E-11 1.90E-11 1.90E-12 -

Rb86 2.40E-03 3.80E-04 1.04E-05 - 1.25E-03 7.49E-04 2.98E-04 -

Rb88 4.08E-01 6.48E-02 1.78E-03 - 5.60E-04 3.36E-04 3.36E-05 -

Rb89 1.87E-02 2.97E-03 8.16E-05 - 2.19E-05 1.32E-05 1.31E-06 -

s132 4.62E-05 7.33E-06 2.01E-07 - 1.88E-05 1.13E-05 2.00E-06 -

s134 4.13E-01 6.56E-02 1.80E-03 - 2.47E-01 1.48E-01 5.93E-01 -

135m 3.13E-04 4.97E-05 1.36E-06 - 1.28E-06 7.68E-07 7.68E-08 -

s136 8.76E-02 1.39E-02 3.82E-04 - 4.31E-02 2.59E-02 7.70E-03 -

s137 2.53E-01 4.02E-02 1.10E-03 - 1.52E-01 9.12E-02 4.23E-01 -

s138 1.50E-01 2.38E-02 6.53E-04 - 3.86E-04 2.32E-04 2.32E-05 -

P32 3.30E-10 4.88E-10 2.98E-11 - 1.65E-10 9.88E-11 3.14E-11 -

Co57 2.46E-12 3.64E-12 2.22E-13 - 1.46E-12 8.77E-13 2.70E-12 -

Sr89 1.47E-05 2.18E-05 1.33E-06 - 1.06E-05 6.35E-06 6.23E-06 -

Sr90 3.31E-06 4.90E-06 2.99E-07 - 1.98E-06 1.19E-06 5.52E-06 -

Sr91 7.54E-06 1.13E-05 6.91E-07 - 3.37E-07 2.02E-07 2.02E-08 -

Sr92 4.03E-06 6.04E-06 3.69E-07 - 4.97E-08 2.98E-08 2.98E-09 -

Y90 8.17E-07 1.19E-06 7.26E-08 - 1.34E-06 8.06E-07 5.48E-06 -

91m 4.04E-06 6.06E-06 3.70E-07 - 2.12E-07 1.27E-07 1.27E-08 -

Y91 2.14E-06 3.16E-06 1.93E-07 - 1.24E-06 7.42E-07 8.32E-07 -

Y92 3.42E-06 5.13E-06 3.14E-07 - 1.06E-07 6.35E-08 6.35E-09 -

Y93 1.61E-06 2.41E-06 1.47E-07 - 7.59E-08 4.55E-08 4.55E-09 -

Zr97 2.37E-06 3.55E-06 2.17E-07 - 1.84E-07 1.10E-07 1.10E-08 -

Nb95 2.37E-05 7.33E-06 3.14E-07 1.53E-04 3.82E-05 2.30E-05 2.46E-04 -

Mo99 4.29E-03 6.38E-03 3.90E-04 - 1.13E-03 6.76E-04 7.86E-05 -

o101 1.60E-04 2.40E-04 1.47E-05 - 1.81E-07 1.09E-07 1.09E-08 -

c99m 3.97E-03 5.90E-03 3.61E-04 - 1.08E-03 6.50E-04 7.56E-05 -

Tc99 1.23E-07 1.83E-07 1.12E-08 - 7.41E-08 4.44E-08 2.09E-07 -

u103 4.12E-06 6.10E-06 3.73E-07 - 2.31E-06 1.39E-06 1.08E-06 -

u105 1.34E-06 2.00E-06 1.22E-07 - 2.75E-08 1.65E-08 1.65E-09 -

u106 2.67E-06 3.96E-06 2.42E-07 - 1.59E-06 9.56E-07 3.28E-06 -

103m 4.08E-06 6.03E-06 3.68E-07 - 2.28E-06 1.37E-06 1.07E-06 -

h105 2.86E-06 4.26E-06 2.60E-07 - 4.83E-07 2.90E-07 2.97E-08 -

2 12.2-31 Revision 4

otope LCW HCW Oil LCW GAC LCW TUF LCW RO LCW Cation LCW Anion Collection Collection Separator Unit Unit Unit Bed Bed Tank Tank (Ci) (Ci) (Ci) (Ci) (Ci) (Ci)

(Ci) (Ci) h106 2.67E-06 3.96E-06 2.42E-07 - 1.59E-06 9.56E-07 3.28E-06 -

g110 2.86E-05 7.38E-06 2.82E-07 1.25E-03 1.62E-05 9.71E-06 2.90E-05 -

b124 6.08E-09 9.00E-09 5.49E-10 5.83E-08 3.49E-09 2.09E-09 2.41E-09 -

b125 5.36E-08 7.93E-08 4.84E-09 6.15E-06 3.21E-08 1.92E-08 8.00E-08 -

b127 2.31E-07 3.43E-07 2.10E-08 1.42E-07 7.46E-08 4.48E-08 5.94E-09 -

b129 2.81E-07 4.22E-07 2.58E-08 8.21E-09 5.74E-09 3.44E-09 3.44E-10 -

125m 7.86E-06 1.16E-05 7.10E-07 1.39E-06 4.50E-06 2.70E-06 2.99E-06 -

127m 2.53E-05 3.75E-05 2.29E-06 2.51E-08 1.48E-05 8.89E-06 1.66E-05 -

e127 9.93E-05 1.48E-04 9.07E-06 1.17E-07 1.78E-05 1.07E-05 1.65E-05 -

129m 7.25E-05 1.07E-04 6.56E-06 1.86E-09 4.02E-05 2.41E-05 1.63E-05 -

e129 1.02E-04 1.52E-04 9.27E-06 6.35E-09 2.57E-05 1.54E-05 1.03E-05 -

131m 2.35E-04 3.51E-04 2.14E-05 - 3.22E-05 1.93E-05 1.96E-06 -

e131 1.15E-04 1.73E-04 1.05E-05 - 7.38E-06 4.43E-06 4.49E-07 -

e132 1.72E-03 2.56E-03 1.56E-04 - 4.99E-04 2.99E-04 3.68E-05 -

133m 1.45E-04 2.18E-04 1.33E-05 - 6.21E-07 3.73E-07 3.73E-08 -

e134 2.07E-04 3.10E-04 1.89E-05 - 6.67E-07 4.00E-07 4.00E-08 -

137m 1.16E-02 1.70E-02 1.04E-03 - 1.44E-01 8.61E-02 4.00E-01 -

a139 3.84E-06 5.77E-06 3.52E-07 - 2.47E-08 1.48E-08 1.48E-09 -

a140 2.12E-05 3.15E-05 1.92E-06 - 1.04E-05 6.23E-06 1.81E-06 -

a140 6.28E-06 9.14E-06 5.57E-07 - 8.71E-06 5.22E-06 1.88E-06 -

a141 1.19E-06 1.79E-06 1.09E-07 - 2.17E-08 1.30E-08 1.30E-09 -

a142 5.69E-07 8.54E-07 5.22E-08 - 4.01E-09 2.40E-09 2.40E-10 -

e141 3.27E-06 4.85E-06 2.96E-07 - 1.81E-06 1.09E-06 7.11E-07 -

e143 2.46E-06 3.67E-06 2.24E-07 - 3.69E-07 2.21E-07 2.26E-08 -

e144 2.75E-06 4.07E-06 2.49E-07 - 1.64E-06 9.81E-07 3.08E-06 -

r143 2.91E-06 4.31E-06 2.63E-07 - 1.54E-06 9.23E-07 2.86E-07 -

r144 2.73E-06 4.03E-06 2.46E-07 - 1.62E-06 9.72E-07 3.05E-06 -

p239 5.17E-05 7.70E-05 4.70E-06 - 1.22E-05 7.31E-06 8.14E-07 -

Na24 5.39E-03 8.07E-03 4.93E-04 - 3.74E-04 2.24E-04 2.24E-05 -

Cr51 4.61E-03 9.26E-04 2.81E-05 2.36E-02 2.52E-03 1.51E-03 8.53E-04 -

Mn54 2.47E-03 4.87E-04 1.45E-05 1.39E-01 1.47E-03 8.81E-04 2.86E-03 -

Fe55 1.85E-03 3.65E-04 1.08E-05 - 1.11E-03 6.66E-04 2.77E-03 -

Fe59 4.53E-04 9.02E-05 2.71E-06 - 2.56E-04 1.54E-04 1.34E-04 -

Co58 6.60E-02 7.78E-03 4.16E-05 8.02E-01 3.81E-02 2.29E-02 3.03E-02 -

Co60 8.19E-04 1.61E-04 4.78E-06 1.20E-01 4.91E-04 2.95E-04 1.30E-03 -

Ni63 4.09E-04 8.06E-05 2.39E-06 - 2.46E-04 1.47E-04 6.89E-04 -

Zn65 7.85E-04 1.55E-04 4.60E-06 - 4.66E-04 2.80E-04 8.26E-04 -

Zr95 5.93E-04 1.18E-04 3.52E-06 - 3.41E-04 2.05E-04 2.49E-04 -

110m 2.01E-03 3.95E-04 1.17E-05 9.22E-02 1.19E-03 7.14E-04 2.13E-03 -

W187 1.36E-03 5.29E-04 2.52E-05 - 1.49E-04 8.93E-05 8.97E-06 -

H3 7.08E+01 1.84E+01 9.96E-01 - - - - -

C14 5.51E-03 6.91E-04 1.21E-05 - - - - -

Assumes the plant consists of 12 NPMs operating on a two-year refueling cycle.

2 12.2-32 Revision 4

Radionuclide Content otope LCW Mixed LCW Cesium LCW HCW GAC HCW TUF HCW RO HCW Drum Dryer Bed Bed Sample Unit Unit Unit Sample (Ci)

(Ci) (Ci) Tank (Ci) (Ci) (Ci) Tank (Ci) (Ci)

Br82 3.19E-09 - 9.27E-12 - 2.01E-05 1.21E-05 3.83E-07 4.09E-05 Br83 1.22E-09 - - - 8.05E-06 4.83E-06 1.55E-21 1.58E-05 Br84 1.25E-10 - - - 8.27E-07 4.96E-07 - 1.63E-06 Br85 1.38E-12 - - - 9.11E-09 5.47E-09 - 1.79E-08 I129 1.39E-11 2.32E-16 2.99E-15 - 1.81E-09 1.09E-09 1.21E-10 1.75E-07 I130 8.90E-09 - 6.57E-13 - 5.85E-05 3.51E-05 2.74E-08 1.15E-04 I131 1.59E-05 1.54E-09 6.70E-08 - 1.22E-02 7.31E-03 6.92E-04 7.90E-02 I132 4.06E-06 3.68E-08 2.20E-09 - 8.81E-04 5.29E-04 3.28E-05 2.75E-03 I133 7.38E-07 3.07E-11 6.15E-10 - 3.84E-03 2.30E-03 2.05E-05 7.93E-03 I134 8.73E-09 4.00E-11 - - 2.96E-05 1.78E-05 - 5.89E-05 I135 1.15E-07 - 2.64E-14 - 7.59E-04 4.55E-04 1.11E-09 1.49E-03 b86m 1.06E-13 9.50E-14 - - 5.22E-12 3.13E-12 - 5.90E-11 Rb86 1.66E-05 1.49E-05 3.92E-07 - 1.99E-04 1.20E-04 1.25E-05 9.26E-03 Rb88 1.87E-06 1.68E-06 - - 9.24E-05 5.54E-05 - 1.04E-03 Rb89 7.30E-08 6.57E-08 - - 3.61E-06 2.17E-06 - 4.08E-05 s132 1.11E-07 9.98E-08 5.18E-09 - 3.02E-06 1.81E-06 1.64E-07 6.20E-05 s134 3.30E-02 2.97E-02 8.23E-05 - 3.93E-02 2.36E-02 2.61E-03 1.84E+01 135m 4.27E-09 3.84E-09 - - 2.11E-07 1.27E-07 - 2.39E-06 s136 4.28E-04 3.85E-04 1.32E-05 - 6.90E-03 4.14E-03 4.19E-04 2.39E-01 s137 2.35E-02 2.12E-02 5.07E-05 - 2.41E-02 1.45E-02 1.61E-03 1.32E+01 s138 1.29E-06 1.16E-06 - - 6.37E-05 3.82E-05 - 7.20E-04 P32 3.45E-12 3.14E-14 1.01E-15 - 2.46E-10 1.47E-10 1.50E-11 2.12E-09 Co57 2.97E-13 2.70E-15 9.71E-18 - 2.16E-12 1.30E-12 1.44E-13 1.83E-10 Sr89 6.15E-07 7.02E-08 7.79E-10 - 1.28E-05 7.66E-06 8.32E-07 3.74E-04 Sr90 6.08E-07 5.52E-09 1.32E-11 - 2.94E-06 1.76E-06 1.96E-07 3.74E-04 Sr91 2.22E-09 2.02E-11 2.68E-15 - 5.24E-07 3.14E-07 4.02E-11 1.38E-06 Sr92 3.28E-10 2.98E-12 - - 7.74E-08 4.64E-08 5.21E-22 2.03E-07 Y90 6.03E-07 5.48E-09 1.08E-11 - 1.96E-06 1.17E-06 1.59E-07 3.71E-04 91m 1.40E-09 1.27E-11 1.71E-15 - 3.29E-07 1.98E-07 2.56E-11 8.65E-07 Y91 9.16E-08 8.32E-10 8.11E-12 - 1.84E-06 1.10E-06 1.20E-07 5.63E-05 Y92 6.98E-10 6.35E-12 5.95E-22 - 1.65E-07 9.89E-08 8.92E-18 4.33E-07 Y93 5.01E-10 4.55E-12 9.46E-16 - 1.18E-07 7.09E-08 1.42E-11 3.10E-07 Zr97 1.22E-09 1.10E-11 4.44E-14 - 2.86E-07 1.72E-07 6.64E-10 7.53E-07 Nb95 2.70E-05 2.46E-07 2.31E-10 4.93E-05 8.89E-06 5.34E-06 4.59E-07 7.92E-03 Mo99 8.65E-06 7.86E-08 4.39E-09 - 1.72E-03 1.03E-03 6.53E-05 5.34E-03 o101 1.19E-09 1.09E-11 - - 2.82E-07 1.69E-07 - 7.40E-07 c99m 8.32E-06 7.56E-08 4.24E-09 - 1.65E-03 9.91E-04 6.31E-05 5.13E-03 Tc99 2.29E-08 2.09E-10 4.94E-13 - 1.10E-07 6.58E-08 7.31E-09 1.41E-05 u103 1.19E-07 1.08E-09 1.50E-11 - 3.43E-06 2.06E-06 2.22E-07 7.30E-05 u105 1.81E-10 1.65E-12 8.73E-21 - 4.28E-08 2.57E-08 1.31E-16 1.12E-07 u106 3.61E-07 3.28E-09 1.06E-11 - 2.36E-06 1.42E-06 1.57E-07 2.22E-04 103m 1.17E-07 1.07E-09 1.48E-11 - 3.39E-06 2.03E-06 2.19E-07 7.21E-05 h105 3.27E-09 2.97E-11 9.62E-13 - 7.45E-07 4.47E-07 1.43E-08 2.02E-06 2 12.2-33 Revision 4

otope LCW Mixed LCW Cesium LCW HCW GAC HCW TUF HCW RO HCW Drum Dryer Bed Bed Sample Unit Unit Unit Sample (Ci)

(Ci) (Ci) Tank (Ci) (Ci) (Ci) Tank (Ci) (Ci) h106 3.61E-07 3.28E-09 1.06E-11 - 2.36E-06 1.42E-06 1.57E-07 2.22E-04 g110 3.19E-06 2.90E-08 3.31E-14 2.57E-04 3.19E-06 1.92E-06 6.52E-11 9.30E-04 b124 2.65E-10 2.41E-12 7.15E-18 8.96E-08 5.17E-09 3.10E-09 4.76E-11 1.63E-07 b125 8.80E-09 8.00E-11 6.68E-17 9.45E-06 4.74E-08 2.85E-08 4.45E-10 5.41E-06 b127 6.53E-10 5.94E-12 1.09E-16 2.19E-07 1.13E-07 6.79E-08 7.32E-10 4.03E-07 b129 3.79E-11 3.44E-13 4.79E-25 1.28E-08 8.94E-09 5.36E-09 3.23E-18 2.35E-08 125m 3.29E-07 2.99E-09 2.95E-11 2.13E-06 6.68E-06 4.01E-06 4.36E-07 2.02E-04 127m 1.83E-06 1.66E-08 9.78E-11 3.87E-08 2.20E-05 1.32E-05 1.45E-06 1.12E-03 e127 1.81E-06 1.65E-08 9.58E-11 1.80E-07 2.66E-05 1.60E-05 1.42E-06 1.11E-03 129m 1.79E-06 1.63E-08 2.60E-10 2.89E-09 5.97E-05 3.58E-05 3.84E-06 1.10E-03 e129 1.13E-06 1.03E-08 1.64E-10 9.90E-09 3.82E-05 2.29E-05 2.42E-06 6.95E-04 131m 2.16E-07 1.96E-09 4.71E-11 - 4.99E-05 2.99E-05 7.03E-07 1.33E-04 e131 4.93E-08 4.49E-10 1.06E-11 - 1.14E-05 6.85E-06 1.58E-07 3.05E-05 e132 4.04E-06 3.68E-08 2.14E-09 - 7.59E-04 4.55E-04 3.18E-05 2.49E-03 133m 4.10E-09 3.73E-11 - - 9.68E-07 5.81E-07 - 2.54E-06 e134 4.40E-09 4.00E-11 - - 1.04E-06 6.24E-07 - 2.73E-06 137m 2.22E-02 2.00E-02 4.78E-05 - 2.28E-02 1.37E-02 1.52E-03 1.24E+01 a139 1.63E-10 1.48E-12 - - 3.84E-08 2.31E-08 - 1.01E-07 a140 1.99E-07 1.81E-09 6.33E-11 - 1.55E-05 9.30E-06 9.38E-07 1.22E-04 a140 2.07E-07 1.88E-09 6.51E-11 - 1.28E-05 7.71E-06 9.64E-07 1.27E-04 a141 1.43E-10 1.30E-12 5.32E-22 - 3.38E-08 2.03E-08 7.98E-18 8.87E-08 a142 2.64E-11 2.40E-13 - - 6.24E-09 3.74E-09 - 1.64E-08 e141 7.82E-08 7.11E-10 1.17E-11 - 2.69E-06 1.62E-06 1.73E-07 4.81E-05 e143 2.48E-09 2.26E-11 6.48E-13 - 5.70E-07 3.42E-07 9.67E-09 1.54E-06 e144 3.39E-07 3.08E-09 1.09E-11 - 2.42E-06 1.45E-06 1.61E-07 2.08E-04 r143 3.15E-08 2.86E-10 9.61E-12 - 2.29E-06 1.38E-06 1.42E-07 1.94E-05 r144 3.36E-07 3.05E-09 1.08E-11 - 2.40E-06 1.44E-06 1.59E-07 2.06E-04 p239 8.95E-08 8.14E-10 4.23E-11 - 1.87E-05 1.12E-05 6.29E-07 5.52E-05 Na24 2.47E-06 2.24E-08 5.32E-11 - 5.81E-04 3.49E-04 7.96E-07 1.53E-03 Cr51 9.38E-05 8.53E-07 6.30E-11 4.92E-03 5.07E-04 3.04E-04 1.26E-07 2.75E-02 Mn54 3.14E-04 2.86E-06 9.12E-11 2.85E-02 2.90E-04 1.74E-04 1.80E-07 9.18E-02 Fe55 3.05E-04 2.77E-06 7.39E-09 - 2.19E-04 1.31E-04 1.46E-05 8.89E-02 Fe59 1.47E-05 1.34E-07 1.66E-09 - 5.11E-05 3.06E-05 3.32E-06 4.31E-03 Co58 3.34E-03 3.03E-05 1.90E-08 9.81E-02 4.50E-03 2.70E-03 2.24E-05 9.08E-01 Co60 1.43E-04 1.30E-06 4.88E-10 2.45E-02 9.66E-05 5.80E-05 9.61E-07 4.17E-02 Ni63 7.58E-05 6.89E-07 1.64E-09 - 4.83E-05 2.90E-05 3.22E-06 2.21E-02 Zn65 9.08E-05 8.26E-07 3.09E-09 - 9.20E-05 5.52E-05 6.10E-06 2.65E-02 Zr95 2.73E-05 2.49E-07 2.24E-09 - 6.78E-05 4.07E-05 4.44E-06 8.00E-03 110m 2.34E-04 2.13E-06 2.43E-12 1.89E-02 2.35E-04 1.41E-04 4.79E-09 6.84E-02 W187 9.87E-07 8.97E-09 1.23E-10 - 6.01E-05 3.61E-05 4.80E-07 3.36E-04 H3 - - 7.07E+01 - - - 1.84E+01 -

C14 - - 5.51E-03 - - - 6.91E-04 -

Assumes the plant consists of 12 NPMs operating on a two-year refueling cycle.

2 12.2-34 Revision 4

cale Final Safety Analysis Report rgy Energy Boundary LCW Collection HCW Oil Separator LCW GAC Unit LCW TUF Unit LCW RO Unit LCW Cation LCW Anion up (MeV) Tank Collection (photon/s) (photon/s) (photon/s) (photon/s) Bed Bed (photon/s) Tank (photon/s) (photon/s)

(photon/s) 1 1.00E-02 - 2.00E-02 9.05E+08 1.99E+08 7.49E+06 6.33E+07 5.42E+07 3.25E+07 1.05E+08 2.01E+05 2 2.00E-02 - 3.00E-02 5.91E+08 2.23E+08 1.08E+07 7.19E+07 5.47E+07 3.28E+07 5.69E+07 1.94E+06 3 3.00E-02 - 4.50E-02 8.62E+08 2.23E+08 9.27E+06 2.70E+07 5.40E+08 3.25E+08 1.16E+09 1.12E+06 4 4.50E-02 - 6.00E-02 3.28E+08 7.41E+07 2.84E+06 1.99E+07 1.63E+07 9.75E+06 2.83E+07 5.46E+04 5 6.00E-02 - 7.00E-02 3.25E+08 5.88E+07 1.86E+06 9.41E+06 8.58E+07 5.16E+07 2.67E+07 2.46E+04 6 7.00E-02 - 7.50E-02 7.43E+07 1.54E+07 5.48E+05 4.02E+06 3.33E+06 2.00E+06 5.32E+06 1.03E+04 7 7.50E-02 - 1.00E-01 4.68E+08 1.06E+08 4.01E+06 1.58E+07 1.01E+08 6.08E+07 3.35E+07 1.43E+06 8 1.00E-01 - 1.50E-01 5.76E+08 3.30E+08 1.80E+07 1.94E+07 5.55E+07 3.34E+07 2.03E+07 3.44E+04 9 1.50E-01 - 2.00E-01 8.11E+08 1.62E+08 5.65E+06 1.06E+07 2.61E+08 1.57E+08 5.39E+07 1.76E+05 0 2.00E-01 - 2.60E-01 2.98E+08 1.53E+08 8.14E+06 1.07E+07 2.28E+07 1.37E+07 1.14E+07 1.95E+04 1 2.60E-01 - 3.00E-01 5.07E+08 1.85E+08 8.81E+06 3.98E+06 2.02E+08 1.21E+08 3.25E+07 3.68E+06 2 3.00E-01 - 4.00E-01 2.44E+09 1.15E+09 5.82E+07 9.22E+07 1.04E+09 6.26E+08 1.27E+08 4.95E+07 3 4.00E-01 - 4.50E-01 3.63E+08 1.59E+08 7.98E+06 1.32E+08 4.03E+06 2.42E+06 3.41E+06 8.01E+04 4 4.50E-01 - 5.10E-01 2.00E+09 3.65E+08 1.17E+07 2.58E+06 1.61E+08 9.62E+07 3.25E+08 2.25E+05 5 5.10E-01 - 5.12E-01 7.37E+08 1.15E+08 2.27E+06 8.84E+09 4.21E+08 2.53E+08 3.35E+08 5.01E+04 6 5.12E-01 - 6.00E-01 4.75E+09 2.11E+09 1.06E+08 1.83E+06 2.25E+09 1.35E+09 5.31E+09 2.34E+06 7 6.00E-01 - 7.00E-01 1.47E+10 3.56E+09 1.43E+08 3.96E+09 1.33E+10 7.95E+09 3.36E+10 4.37E+06 8 7.00E-01 - 8.00E-01 1.49E+10 2.87E+09 9.69E+07 1.49E+09 8.78E+09 5.26E+09 2.10E+10 1.15E+06 9 8.00E-01 - 9.00E-01 7.56E+09 1.71E+09 6.27E+07 3.62E+10 3.18E+09 1.91E+09 2.38E+09 2.30E+05 0 9.00E-01 - 1.00E+00 1.22E+09 3.29E+08 1.39E+07 1.16E+09 2.08E+07 1.25E+07 2.71E+07 3.34E+04 1 1.00E+00 - 1.20E+00 4.80E+09 1.20E+09 4.86E+07 4.74E+09 1.35E+09 8.11E+08 8.80E+08 1.94E+05 2 1.20E+00 - 1.33E+00 1.11E+09 5.07E+08 2.58E+07 2.34E+09 3.32E+08 1.99E+08 8.35E+07 2.38E+05 3 1.33E+00 - 1.44E+00 5.32E+09 1.16E+09 4.36E+07 2.99E+09 3.19E+08 1.91E+08 6.97E+08 1.44E+04 4 1.44E+00 - 1.50E+00 9.60E+07 1.06E+08 6.19E+06 1.43E+08 2.94E+06 1.76E+06 3.33E+06 4.15E+04 5 1.50E+00 - 1.57E+00 6.47E+07 3.41E+07 1.79E+06 4.98E+08 8.52E+06 5.12E+06 1.18E+07 1.05E+04 Radiation Sources 6 1.57E+00 - 1.66E+00 1.90E+07 1.69E+07 9.62E+05 8.31E+05 3.98E+05 2.39E+05 8.91E+04 1.09E+03 7 1.66E+00 - 1.80E+00 1.41E+08 2.14E+08 1.27E+07 1.49E+08 8.71E+06 5.24E+06 5.64E+06 9.16E+04 8 1.80E+00 - 2.00E+00 3.35E+09 5.65E+08 1.67E+07 5.82E+05 5.10E+06 3.06E+06 3.18E+05 6.32E+03 9 2.00E+00 - 2.15E+00 1.34E+08 3.46E+07 1.43E+06 3.58E+04 4.26E+05 2.56E+05 2.44E+04 4.63E+03 0 2.15E+00 - 2.35E+00 9.43E+08 1.58E+08 4.65E+06 5.11E+04 2.41E+06 1.45E+06 1.44E+05 3.08E+03

cale Final Safety Analysis Report rgy Energy Boundary LCW Collection HCW Oil Separator LCW GAC Unit LCW TUF Unit LCW RO Unit LCW Cation LCW Anion up (MeV) Tank Collection (photon/s) (photon/s) (photon/s) (photon/s) Bed Bed (photon/s) Tank (photon/s) (photon/s)

(photon/s) 1 2.35E+00 - 2.50E+00 2.19E+07 1.45E+07 7.96E+05 7.34E+02 1.42E+05 8.54E+04 5.19E+03 4.58E+03 2 2.50E+00 - 2.75E+00 1.02E+09 3.02E+08 1.36E+07 4.25E+01 9.05E+06 5.42E+06 5.44E+05 6.74E+01 3 2.75E+00 - 3.00E+00 1.28E+08 1.48E+08 8.88E+06 2.28E+01 6.67E+06 3.99E+06 3.99E+05 1.12E+01 4 3.00E+00 - 3.50E+00 1.02E+08 1.71E+07 5.01E+05 - 1.73E+05 1.04E+05 1.04E+04 3.49E+01 5 3.50E+00 - 4.00E+00 1.96E+07 4.13E+06 1.51E+05 - 3.96E+04 2.37E+04 2.34E+03 3.28E+01 6 4.00E+00 - 4.50E+00 3.91E+06 6.54E+05 1.92E+04 - 6.49E+03 3.89E+03 3.88E+02 1.24E+00 7 4.50E+00 - 5.00E+00 2.87E+07 4.55E+06 1.25E+05 - 3.94E+04 2.36E+04 2.36E+03 1.24E-06 8 5.00E+00 - 5.50E+00 5.41E+04 8.59E+03 2.36E+02 - 7.43E+01 4.46E+01 4.46E+00 1.12E-06 9 5.50E+00 - 6.00E+00 - - - - - - - -

0 6.00E+00 - 6.50E+00 - - - - - - - -

1 6.50E+00 - 7.00E+00 - - - - - - - -

2 7.00E+00 - 7.50E+00 - - - - - - - -

3 7.50E+00 - 8.00E+00 - - - - - - - -

4 8.00E+00 - 1.00E+01 - - - - - - - -

5 1.00E+01 - 1.20E+01 - - - - - - - -

6 1.20E+01 - 1.40E+01 - - - - - - - -

7 1.40E+01 - 2.00E+01 - - - - - - - -

tal 7.17E+10 1.86E+10 7.66E+08 6.30E+10 3.26E+10 1.95E+10 6.62E+10 6.73E+07

Assumes the plant consists of 12 NPMs operating on a two-year refueling cycle.

Radiation Sources

cale Final Safety Analysis Report rgy Energy Boundary LCW Mixed LCW Cesium LCW Sample HCW GAC Unit HCW TUF Unit HCW RO Unit HCW Sample Drum Dryer up (MeV) Bed Bed Tank (photon/s) (photon/s) (photon/s) Tank (photon/s)

(photon/s) (photon/s) (photon/s) (photon/s) 1 1.00E-02 - 2.00E-02 6.00E+06 5.15E+06 2.21E+06 8.61E+06 1.85E+07 1.11E+07 1.41E+06 3.30E+09 2 2.00E-02 - 3.00E-02 3.38E+06 2.67E+06 5.46E+04 1.25E+07 4.28E+07 2.57E+07 2.05E+06 1.93E+09 3 3.00E-02 - 4.50E-02 6.45E+07 5.80E+07 1.99E+05 3.65E+06 9.85E+07 5.91E+07 6.18E+06 3.60E+10 4 4.50E-02 - 6.00E-02 1.62E+06 1.37E+06 1.62E+04 2.64E+06 7.18E+06 4.30E+06 3.23E+05 8.90E+08 5 6.00E-02 - 7.00E-02 1.51E+06 1.32E+06 2.97E+04 1.24E+06 1.45E+07 8.69E+06 8.37E+05 8.32E+08 6 7.00E-02 - 7.50E-02 3.06E+05 2.57E+05 2.07E+03 5.27E+05 9.14E+05 5.49E+05 3.15E+04 1.66E+08 7 7.50E-02 - 1.00E-01 1.91E+06 1.65E+06 3.00E+04 2.05E+06 2.62E+07 1.57E+07 1.51E+06 1.12E+09 8 1.00E-01 - 1.50E-01 1.34E+06 8.27E+05 3.68E+03 2.76E+06 6.91E+07 4.15E+07 2.65E+06 7.45E+08 9 1.50E-01 - 2.00E-01 3.04E+06 2.66E+06 7.84E+04 1.36E+06 4.74E+07 2.84E+07 2.74E+06 1.69E+09 0 2.00E-01 - 2.60E-01 7.20E+05 4.96E+05 1.80E+03 1.75E+06 2.69E+07 1.61E+07 1.10E+06 4.01E+08 1 2.60E-01 - 3.00E-01 1.86E+06 1.62E+06 5.33E+04 6.05E+05 5.87E+07 3.52E+07 3.33E+06 1.20E+09 2 3.00E-01 - 4.00E-01 7.73E+06 6.17E+06 2.06E+05 1.87E+07 4.96E+08 2.97E+08 2.84E+07 6.43E+09 3 4.00E-01 - 4.50E-01 3.59E+05 1.83E+04 4.22E+01 2.70E+07 4.40E+06 2.64E+06 4.41E+04 1.18E+08 4 4.50E-01 - 5.10E-01 1.81E+07 1.63E+07 5.00E+04 4.42E+05 2.99E+07 1.79E+07 1.80E+06 1.01E+10 5 5.10E-01 - 5.12E-01 3.69E+07 3.35E+05 2.15E+02 1.08E+09 5.24E+07 3.14E+07 2.69E+05 1.00E+10 6 5.12E-01 - 6.00E-01 2.95E+08 2.66E+08 7.36E+05 3.58E+05 4.80E+08 2.88E+08 2.42E+07 1.65E+11 7 6.00E-01 - 7.00E-01 1.87E+09 1.68E+09 4.38E+06 8.12E+08 2.18E+09 1.31E+09 1.43E+08 1.04E+12 8 7.00E-01 - 8.00E-01 1.17E+09 1.05E+09 2.90E+06 3.05E+08 1.44E+09 8.65E+08 9.42E+07 6.51E+11 9 8.00E-01 - 9.00E-01 2.00E+08 5.85E+07 5.43E+05 5.08E+09 4.71E+08 2.83E+08 1.82E+07 7.30E+10 0 9.00E-01 - 1.00E+00 2.97E+06 3.19E+04 1.79E+01 2.37E+08 1.11E+07 6.64E+06 2.49E+05 8.84E+08 1 1.00E+00 - 1.20E+00 5.27E+07 4.06E+07 4.08E+05 9.67E+08 2.31E+08 1.39E+08 1.33E+07 2.74E+10 2 1.20E+00 - 1.33E+00 6.15E+06 2.82E+06 9.59E+04 4.78E+08 6.86E+07 4.11E+07 3.20E+06 2.65E+09 3 1.33E+00 - 1.44E+00 4.12E+07 3.28E+07 9.06E+04 6.11E+08 7.38E+07 4.43E+07 3.04E+06 2.17E+10 4 1.44E+00 - 1.50E+00 3.66E+05 3.84E+03 1.39E+00 2.93E+07 3.57E+06 2.14E+06 2.14E+04 1.13E+08 5 1.50E+00 - 1.57E+00 1.28E+06 2.81E+04 5.62E+02 1.02E+08 2.30E+06 1.38E+06 1.90E+04 3.81E+08 6 1.57E+00 - 1.66E+00 9.72E+03 1.78E+02 2.39E+00 1.70E+05 5.80E+05 3.49E+05 3.54E+04 5.41E+06 Radiation Sources 7 1.66E+00 - 1.80E+00 6.22E+05 6.05E+03 4.04E+00 1.83E+07 7.08E+06 4.25E+06 1.20E+04 1.81E+08 8 1.80E+00 - 2.00E+00 2.00E+04 1.39E+04 1.75E+00 1.19E+05 1.76E+06 1.06E+06 2.39E+04 1.17E+07 9 2.00E+00 - 2.15E+00 2.09E+03 5.99E+02 6.73E-01 7.50E+03 5.82E+05 3.49E+05 1.00E+04 1.79E+06 0 2.15E+00 - 2.35E+00 8.44E+03 6.87E+03 3.20E-01 1.04E+04 6.96E+05 4.18E+05 4.76E+03 5.12E+06 1 2.35E+00 - 2.50E+00 5.06E+02 1.04E+02 1.77E-01 1.51E+02 3.67E+05 2.20E+05 2.63E+03 8.70E+05

cale Final Safety Analysis Report rgy Energy Boundary LCW Mixed LCW Cesium LCW Sample HCW GAC Unit HCW TUF Unit HCW RO Unit HCW Sample Drum Dryer up (MeV) Bed Bed Tank (photon/s) (photon/s) (photon/s) Tank (photon/s)

(photon/s) (photon/s) (photon/s) (photon/s) 2 2.50E+00 - 2.75E+00 5.41E+04 5.77E+03 1.15E+00 8.81E+00 1.16E+07 6.96E+06 1.73E+04 3.32E+07 3 2.75E+00 - 3.00E+00 4.39E+04 5.52E+02 9.43E-01 4.73E+00 1.03E+07 6.18E+06 1.41E+04 2.72E+07 4 3.00E+00 - 3.50E+00 5.79E+02 5.17E+02 6.74E-04 - 3.10E+04 1.86E+04 9.98E+00 3.27E+05 5 3.50E+00 - 4.00E+00 1.65E+02 8.62E+01 1.50E-03 - 2.33E+04 1.40E+04 2.25E+01 1.01E+05 6 4.00E+00 - 4.50E+00 2.20E+01 1.91E+01 1.65E-05 - 1.31E+03 7.86E+02 2.47E-01 1.25E+04 7 4.50E+00 - 5.00E+00 1.31E+02 1.18E+02 - - 6.49E+03 3.89E+03 - 7.31E+04 8 5.00E+00 - 5.50E+00 2.48E-01 2.23E-01 - - 1.23E+01 7.35E+00 - 1.38E+02 9 5.50E+00 - 6.00E+00 - - - - - - - -

0 6.00E+00 - 6.50E+00 - - - - - - - -

1 6.50E+00 - 7.00E+00 - - - - - - - -

2 7.00E+00 - 7.50E+00 - - - - - - - -

3 7.50E+00 - 8.00E+00 - - - - - - - -

4 8.00E+00 - 1.00E+01 - - - - - - - -

5 1.00E+01 - 1.20E+01 - - - - - - - -

6 1.20E+01 - 1.40E+01 - - - - - - - -

7 1.40E+01 - 2.00E+01 - - - - - - - -

tal 3.79E+09 3.22E+09 1.21E+07 9.81E+09 5.99E+09 3.59E+09 3.52E+08 2.06E+12

Assumes the plant consists of 12 NPMs operating on a two-year refueling cycle.

Radiation Sources

Model Parameter Value S guard bed ontents eometry vertical cylinder Source dimensions of vessel diameter=1.79; height=47.5 Shield thickness of steel shell 0.25 S decay bed (four each per train; two trains) puts eometry vertical cylinder Source dimensions of vessel diameter=1.79; height=15 Shield thickness of steel shell 0.25 2 12.2-39 Revision 4

Radionuclide Content Guard Bed Decay Bed 5A Decay Bed 6A Decay Bed 7A Decay Bed 8A Isotope (Ci) (Ci) (Ci) (Ci) (Ci)

Kr83m 1.37E-03 1.93E-03 2.81E-05 6.06E-07 3.12E-08 Kr85m 7.81E-03 1.67E-02 2.86E-03 4.91E-04 8.41E-05 Kr85 2.93E+00 1.06E+01 1.06E+01 1.05E+01 1.05E+01 Kr87 2.57E-03 3.12E-03 6.24E-06 1.25E-08 2.50E-11 Kr88 1.09E-02 1.91E-02 1.18E-03 7.31E-05 4.52E-06 Kr89 8.59E-06 8.59E-06 - - -

Xe131m 8.22E-01 2.37E+00 1.23E+00 6.36E-01 3.29E-01 Xe133m 5.23E-01 8.10E-01 2.31E-02 6.58E-04 1.90E-05 Xe133 5.05E+01 1.16E+02 2.67E+01 6.04E+00 1.37E+00 Xe135m 4.22E-04 4.22E-04 3.72E-05 3.72E-06 3.72E-07 Xe135 3.64E-01 3.66E-01 6.43E-04 5.94E-05 5.94E-06 Xe137 3.34E-05 3.34E-05 - - -

Xe138 4.22E-04 4.22E-04 - - -

Br82 5.56E-06 5.56E-06 5.56E-07 5.56E-08 5.56E-09 Br83 2.16E-06 2.16E-06 2.16E-07 2.16E-08 2.16E-09 Br84 2.22E-07 2.22E-07 2.22E-08 2.22E-09 2.22E-10 Br85 2.45E-09 2.45E-09 2.45E-10 2.45E-11 2.45E-12 I129 1.42E-06 1.42E-06 1.42E-07 1.42E-08 1.42E-09 I130 1.57E-05 1.57E-05 1.57E-06 1.57E-07 1.57E-08 I131 6.30E-03 6.30E-03 6.30E-04 6.30E-05 6.30E-06 I132 3.43E-05 3.43E-05 3.43E-06 3.43E-07 3.43E-08 I133 1.03E-03 1.03E-03 1.03E-04 1.03E-05 1.03E-06 I134 7.68E-06 7.68E-06 7.68E-07 7.68E-08 7.68E-09 I135 2.04E-04 2.04E-04 2.04E-05 2.04E-06 2.04E-07 Rb88 1.09E-02 1.91E-02 1.18E-03 7.31E-05 4.52E-06 Rb89 8.59E-06 8.59E-06 - - -

Cs137 2.50E-05 2.50E-05 - - -

Cs138 4.22E-04 4.22E-04 - - -

Sr89 8.59E-06 8.59E-06 - - -

Ba137m 2.36E-05 2.36E-05 - - -

Ar41 1.37E-02 3.96E-02 2.06E-02 1.07E-02 5.55E-03

Assumes the plant consists of 12 NPMs operating on a two-year refueling cycle.

2 12.2-40 Revision 4

Strengths nergy Energy Boundary Guard Bed Decay Bed 5A Decay Bed 6A Decay Bed 7A Decay Bed 8A roup (MeV) (photons/s) (photons/s) (photons/s) (photons/s) (photons/s) 1 1.00E 2.00E-02 3.46E+09 8.42E+09 3.23E+09 2.06E+09 1.80E+09 2 2.00E 3.00E-02 1.98E+10 4.67E+10 1.83E+10 9.51E+09 5.30E+09 3 3.00E 4.50E-02 7.84E+11 1.80E+12 4.19E+11 9.79E+10 2.40E+10 4 4.50E 6.00E-02 7.64E+08 1.90E+09 8.07E+08 5.61E+08 5.05E+08 5 6.00E 7.00E-02 3.25E+08 8.12E+08 3.56E+08 2.54E+08 2.31E+08 6 7.00E 7.50E-02 1.32E+08 3.30E+08 1.47E+08 1.06E+08 9.69E+07 7 7.50E 1.00E-01 6.62E+11 1.52E+12 3.50E+11 7.95E+10 1.82E+10 8 1.00E 1.50E-01 4.50E+08 1.10E+09 4.76E+08 3.51E+08 3.25E+08 9 1.50E 2.00E-01 2.07E+09 4.99E+09 1.68E+09 7.51E+08 4.29E+08 10 2.00E 2.60E-01 1.52E+10 1.65E+10 1.97E+08 8.43E+07 7.84E+07 11 2.60E 3.00E-01 8.28E+07 1.76E+08 6.32E+07 4.04E+07 3.53E+07 12 3.00E 4.00E-01 3.92E+08 5.96E+08 1.30E+08 6.26E+07 5.06E+07 13 4.00E 4.50E-01 1.01E+08 1.17E+08 7.60E+06 7.11E+06 7.05E+06 14 4.50E 5.10E-01 1.32E+07 1.98E+07 4.42E+06 3.77E+06 3.70E+06 15 5.10E 5.12E-01 2.37E+08 8.49E+08 8.48E+08 8.48E+08 8.48E+08 16 5.12E 6.00E-01 2.67E+08 8.30E+08 7.84E+08 7.80E+08 7.80E+08 17 6.00E 7.00E-01 3.97E+08 4.02E+08 3.37E+06 6.93E+05 4.30E+05 18 7.00E 8.00E-01 1.90E+07 2.27E+07 1.23E+06 1.16E+05 1.74E+04 19 8.00E 9.00E-01 1.09E+08 1.77E+08 9.87E+06 6.29E+05 4.31E+04 20 9.00E 1.00E+00 3.75E+07 6.48E+07 3.99E+06 2.52E+05 1.69E+04 21 1.00E+00 - 1.20E+00 2.67E+07 3.92E+07 2.10E+06 1.44E+05 1.09E+04 22 1.20E+00 - 1.33E+00 5.27E+08 1.51E+09 7.74E+08 4.01E+08 2.08E+08 23 1.33E+00 - 1.44E+00 2.53E+07 3.42E+07 1.27E+06 7.96E+04 5.10E+03 24 1.44E+00 - 1.50E+00 1.56E+06 1.99E+06 1.34E+05 1.11E+04 1.00E+03 25 1.50E+00 - 1.57E+00 5.33E+07 9.29E+07 5.72E+06 3.55E+05 2.20E+04 26 1.57E+00 - 1.66E+00 2.84E+06 4.76E+06 2.71E+05 1.69E+04 1.10E+03 27 1.66E+00 - 1.80E+00 1.13E+07 1.58E+07 1.06E+06 2.46E+05 1.06E+05 28 1.80E+00 - 2.00E+00 9.06E+07 1.58E+08 9.75E+06 6.04E+05 3.74E+04 29 2.00E+00 - 2.15E+00 4.09E+07 6.79E+07 3.82E+06 2.37E+05 1.47E+04 30 2.15E+00 - 2.35E+00 7.12E+07 1.23E+08 7.39E+06 4.58E+05 2.83E+04 31 2.35E+00 - 2.50E+00 1.40E+08 2.46E+08 1.52E+07 9.39E+05 5.81E+04 32 2.50E+00 - 2.75E+00 2.60E+07 3.80E+07 1.38E+06 8.39E+04 5.18E+03 33 2.75E+00 - 3.00E+00 1.66E+06 2.69E+06 1.37E+05 8.44E+03 5.22E+02 34 3.00E+00 - 3.50E+00 2.43E+06 3.91E+06 1.99E+05 1.23E+04 7.58E+02 35 3.50E+00 - 4.00E+00 3.62E+05 6.08E+05 3.51E+04 2.17E+03 1.35E+02 36 4.00E+00 - 4.50E+00 6.84E+04 1.16E+05 6.83E+03 4.23E+02 2.62E+01 37 4.50E+00 - 5.00E+00 7.66E+05 1.34E+06 8.29E+04 5.14E+03 3.18E+02 38 5.00E+00 - 5.50E+00 1.45E+03 2.53E+03 1.57E+02 9.69E+00 5.99E-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 - - - - -

2 12.2-41 Revision 4

nergy Energy Boundary Guard Bed Decay Bed 5A Decay Bed 6A Decay Bed 7A Decay Bed 8A roup (MeV) (photons/s) (photons/s) (photons/s) (photons/s) (photons/s) 45 1.00E+01 - 1.20E+01 - - - - -

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

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

Total 1.49E+12 3.41E+12 7.97E+11 1.93E+11 5.29E+10

Assumes the plant consists of 12 NPMs operating on a two-year refueling cycle.

2 12.2-42 Revision 4

Model Parameter Value t resin storage tank:

ontents spent resins from CVCS and PCUS eometry vertical cylinder Source dimensions of vessel diameter=12.0; height=7.94 Shield thickness of steel shell 0.25 e separator tank:

puts spent resins from LRWS eometry vertical cylinder Source dimensions of vessel diameter=10.0; height=1.36 Shield thickness of steel shell 0.25 Integrity Container (HIC):

puts spent resins from SRST eometry vertical cylinder Source dimensions of container diameter=4.92' height=5.83' Array of HICs one layer of five Class B/C HICs 2 12.2-43 Revision 4

Content SRST PST HIC Isotope (Ci) (Ci) (Ci) m 1.75E-10 - -

m 3.98E-11 - -

4.57E-08 1.48E-19 3.37E-09 1m 2.60E-01 2.03E-14 1.03E-19 3m 9.05E-03 - -

3 7.41E-01 - -

5m 1.18E-05 - -

5 7.85E-04 - -

4.86E-04 3.22E-07 -

7.99E-11 1.23E-07 -

- 1.27E-08 -

- 1.40E-10 -

3.39E-03 2.81E-09 2.82E-04 9.24E-05 8.99E-07 -

1.14E+01 1.59E-03 -

8.18E-02 4.28E-05 -

8.91E-02 7.42E-05 -

2.43E-08 4.82E-07 -

6.92E-05 1.16E-05 -

m 1.48E-14 2.10E-12 -

1.90E-01 3.30E-04 9.83E-14 4.58E-06 3.71E-05 -

1.53E-07 1.45E-06 -

2 4.09E-04 2.21E-06 -

4 1.14E+04 1.13E+00 5.01E+02 5m 3.12E-08 8.49E-08 -

6 3.40E+00 8.51E-03 3.78E-17 7 1.22E+04 9.26E-01 9.69E+02 8 5.93E-06 2.56E-05 -

4.11E-07 3.49E-11 7.72E-23 7 8.56E-07 4.19E-12 1.21E-08 2.48E-01 6.97E-06 1.52E-06 5.26E+00 1.21E-05 4.19E-01 3.91E-07 2.24E-08 -

3.07E-09 3.31E-09 -

5.26E+00 1.21E-05 4.19E-01 m 2.49E-07 1.41E-08 -

4.85E-02 9.37E-07 1.09E-06 1.21E-08 7.05E-09 -

1.08E-07 5.06E-09 -

1.26E-06 1.23E-08 -

5 2.70E+00 2.85E-04 2.08E-04 9 1.36E-01 8.74E-05 -

01 1.02E-09 1.21E-08 -

2 12.2-44 Revision 4

SRST PST HIC Isotope (Ci) (Ci) (Ci) m 1.31E-01 8.40E-05 -

2.06E-01 4.64E-07 1.72E-02 3 4.12E-02 1.20E-06 1.64E-08 5 3.11E-09 1.83E-09 -

6 1.35E+00 5.50E-06 3.11E-02 3m 4.08E-02 1.19E-06 1.62E-08 5 1.86E-05 3.31E-08 -

6 1.35E+00 5.50E-06 3.11E-02 10 7.12E-01 4.39E-05 8.65E-03 4 1.45E-04 2.71E-09 4.08E-09 5 5.55E-02 1.58E-07 2.87E-03 7 1.65E-05 6.60E-09 -

9 6.40E-10 3.82E-10 -

5m 1.83E-01 3.38E-06 7.07E-04 7m 1.95E+00 2.03E-05 1.97E-03 7 1.91E+00 2.01E-05 1.93E-03 9m 5.29E-01 1.81E-05 2.67E-08 9 3.34E-01 1.14E-05 1.69E-08 1m 8.85E-04 2.18E-06 -

1 1.99E-04 4.98E-07 -

2 7.93E-02 4.09E-05 -

3m 1.33E-08 4.14E-08 -

4 1.08E-08 4.45E-08 -

7m 1.15E+04 8.74E-01 9.15E+02 9 7.92E-10 1.64E-09 -

0 2.09E-02 2.01E-06 7.24E-20 0 2.40E-02 2.09E-06 8.33E-20 1 2.05E-09 1.44E-09 -

2 1.41E-10 2.67E-10 -

1 2.23E-02 7.90E-07 6.98E-10 3 1.23E-05 2.51E-08 -

4 1.02E+00 4.83E-06 1.57E-02 3 3.58E-03 3.18E-07 1.20E-19 4 1.01E+00 4.78E-06 1.55E-02 39 1.12E-03 9.04E-07 -

4 1.30E-03 2.49E-05 -

5.04E+00 9.47E-04 1.21E-08 4 8.33E+01 4.59E-03 1.49E+00 1.44E+02 5.46E-03 7.42E+00 9.42E-01 1.49E-04 1.58E-06 8 1.53E+02 3.47E-02 1.43E-02 0 7.85E+01 2.71E-03 5.10E+00 4.92E+01 1.53E-03 4.05E+00 1.99E+01 1.24E-03 2.32E-01 2.10E+00 2.82E-04 9.54E-05 2 12.2-45 Revision 4

SRST PST HIC Isotope (Ci) (Ci) (Ci) 10m 5.24E+01 3.22E-03 6.36E-01 7 3.21E-02 9.97E-06 -

l 3.56E+04 2.99E+00 2.40E+03

Assumes the plant consists of 12 NPMs operating on a two-year refueling cycle.

2 12.2-46 Revision 4

Strengths Spent Resin Phase Separator High Integrity Energy Boundary Storage Tank Tank Container (HIC) nergy Group (MeV) (photon/s) (photon/s) (photon/s) 1 1.00E 2.00E-02 2.41E+12 2.11E+08 1.51E+11 2 2.00E 3.00E-02 1.33E+12 1.14E+08 7.86E+10 3 3.00E 4.50E-02 3.11E+13 2.46E+09 2.35E+12 4 4.50E 6.00E-02 6.40E+11 5.64E+07 3.99E+10 5 6.00E 7.00E-02 2.94E+11 4.08E+07 1.79E+10 6 7.00E 7.50E-02 1.20E+11 1.06E+07 7.45E+09 7 7.50E 1.00E-01 4.56E+11 5.53E+07 2.66E+10 8 1.00E 1.50E-01 3.83E+11 3.70E+07 2.29E+10 9 1.50E 2.00E-01 2.09E+11 6.70E+07 1.14E+10 10 2.00E 2.60E-01 2.05E+11 2.08E+07 1.00E+10 11 2.60E 3.00E-01 7.66E+10 4.11E+07 2.20E+09 12 3.00E 4.00E-01 5.40E+11 1.95E+08 5.41E+09 13 4.00E 4.50E-01 8.24E+10 5.31E+06 1.34E+09 14 4.50E 5.10E-01 6.18E+12 6.16E+08 2.71E+11 15 5.10E 5.12E-01 1.72E+12 3.84E+08 6.37E+08 16 5.12E 6.00E-01 1.02E+14 1.01E+10 4.48E+12 17 6.00E 7.00E-01 7.75E+14 6.77E+10 4.79E+13 18 7.00E 8.00E-01 4.03E+14 3.99E+10 1.77E+13 19 8.00E 9.00E-01 2.74E+13 3.48E+09 8.33E+11 20 9.00E 1.00E+00 6.57E+11 4.08E+07 7.98E+09 21 1.00E+00 - 1.20E+00 1.55E+13 1.53E+09 7.31E+11 22 1.20E+00 - 1.33E+00 1.57E+12 1.17E+08 9.93E+10 23 1.33E+00 - 1.44E+00 1.44E+13 1.32E+09 6.48E+11 24 1.44E+00 - 1.50E+00 8.13E+10 5.07E+06 9.87E+08 25 1.50E+00 - 1.57E+00 2.83E+11 1.78E+07 3.44E+09 26 1.57E+00 - 1.66E+00 1.32E+09 1.08E+05 6.12E+06 27 1.66E+00 - 1.80E+00 2.87E+10 6.56E+06 7.63E+06 28 1.80E+00 - 2.00E+00 4.30E+08 3.63E+05 4.97E+06 29 2.00E+00 - 2.15E+00 6.65E+07 3.20E+04 7.38E+05 30 2.15E+00 - 2.35E+00 3.11E+08 1.63E+05 6.28E+06 31 2.35E+00 - 2.50E+00 3.95E+07 1.04E+04 6.71E+05 32 2.50E+00 - 2.75E+00 6.31E+07 6.04E+05 1.39E+05 33 2.75E+00 - 3.00E+00 2.61E+07 4.44E+05 5.64E+04 34 3.00E+00 - 3.50E+00 1.12E+06 1.15E+04 2.00E+04 35 3.50E+00 - 4.00E+00 3.73E+04 2.63E+03 8.31E+00 36 4.00E+00 - 4.50E+00 4.71E+02 4.30E+02 -

37 4.50E+00 - 5.00E+00 3.22E+02 2.61E+03 -

38 5.00E+00 - 5.50E+00 6.07E-01 4.92E+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 - - -

2 12.2-47 Revision 4

Spent Resin Phase Separator High Integrity Energy Boundary Storage Tank Tank Container (HIC) nergy Group (MeV) (photon/s) (photon/s) (photon/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 1.39E+15 1.29E+11 7.54E+13

Assumes the plant consists of 12 NPMs operating on a two-year refueling cycle.

2 12.2-48 Revision 4

Gamma Energy Boundaries Single Spent Fuel Assembly Gamma Source for Full Fuel (MeV) Gamma Source Storage Racks (1184)

(photons/sec) (photons/sec) 1.00E-02 - 2.00E-02 2.79E+17 3.30E+20 2.00E-02 - 3.00E-02 1.13E+17 1.34E+20 3.00E-02 - 4.50E-02 1.15E+17 1.36E+20 4.50E-02 - 6.00E-02 5.75E+16 6.80E+19 6.00E-02 - 7.00E-02 3.59E+16 4.25E+19 7.00E-02 - 7.50E-02 8.02E+16 9.50E+19 7.50E-02 - 1.00E-01 7.87E+16 9.31E+19 1.00E-01 - 1.50E-01 1.79E+17 2.12E+20 1.50E-01 - 2.00E-01 7.69E+16 9.11E+19 2.00E-01 - 2.60E-01 8.77E+16 1.04E+20 2.60E-01 - 3.00E-01 6.90E+16 8.17E+19 3.00E-01 - 4.00E-01 1.05E+17 1.24E+20 4.00E-01 - 4.50E-01 4.35E+16 5.16E+19 4.50E-01 - 5.10E-01 5.75E+16 6.81E+19 5.10E-01 - 5.12E-01 2.47E+15 2.93E+18 5.12E-01 - 6.00E-01 8.58E+16 1.02E+20 6.00E-01 - 7.00E-01 7.91E+16 9.36E+19 7.00E-01 - 8.00E-01 8.90E+16 1.05E+20 8.00E-01 - 9.00E-01 7.69E+16 9.11E+19 9.00E-01 - 1.00E+00 5.22E+16 6.18E+19 1.00E+00 - 1.20E+00 6.59E+16 7.81E+19 1.20E+00 - 1.33E+00 4.06E+16 4.81E+19 1.33E+00 - 1.44E+00 3.94E+16 4.67E+19 1.44E+00 - 1.50E+00 7.86E+15 9.30E+18 1.50E+00 - 1.57E+00 1.15E+16 1.36E+19 1.57E+00 - 1.66E+00 1.93E+16 2.28E+19 1.66E+00 - 1.80E+00 1.87E+16 2.22E+19 1.80E+00 - 2.00E+00 1.78E+16 2.10E+19 2.00E+00 - 2.15E+00 1.20E+16 1.42E+19 2.15E+00 - 2.35E+00 1.35E+16 1.59E+19 2.35E+00 - 2.50E+00 9.65E+15 1.14E+19 2.50E+00 - 2.75E+00 1.38E+16 1.63E+19 2.75E+00 - 3.00E+00 8.41E+15 9.96E+18 3.00E+00 - 3.50E+00 1.01E+16 1.19E+19 3.50E+00 - 4.00E+00 5.51E+15 6.52E+18 4.00E+00 - 4.50E+00 3.55E+15 4.20E+18 4.50E+00 - 5.00E+00 1.41E+15 1.67E+18 5.00E+00 - 5.50E+00 1.15E+15 1.36E+18 5.50E+00 - 6.00E+00 6.38E+14 7.55E+17 6.00E+00 - 6.50E+00 1.71E+14 2.02E+17 6.50E+00 - 7.00E+00 1.01E+13 1.19E+16 7.00E+00 - 7.50E+00 4.15E+12 4.92E+15 7.50E+00 - 8.00E+00 9.11E+10 1.08E+14 8.00E+00 - 1.00E+01 6.02E+10 7.13E+13 1.00E+01 - 1.20E+01 9.10E+06 1.08E+10 2 12.2-49 Revision 4

Gamma Energy Boundaries Single Spent Fuel Assembly Gamma Source for Full Fuel (MeV) Gamma Source Storage Racks (1184)

(photons/sec) (photons/sec) 1.20E+01 - 1.40E+01 1.08E+05 1.28E+08 1.40E+01 - 2.00E+01 1.87E+00 2.21E+03 Total 2.06E+18 2.444E+21 2 12.2-50 Revision 4

Neutron Energy Boundaries Single Spent Fuel Assembly Neutron Source for Full Fuel (MeV) Neutron Source Storage Racks (neutrons/sec) (1184 assemblies)

(neutrons/sec) 1.00E-11 - 1.00E-08 4.46E+07 5.28E+10 1.00E-08 - 3.00E-08 8.93E+07 1.06E+11 3.00E-08 - 5.00E-08 8.93E+07 1.06E+11 5.00E-08 - 1.00E-07 2.23E+08 2.64E+11 1.00E-07 - 2.25E-07 5.58E+08 6.61E+11 2.25E-07 - 3.25E-07 4.46E+08 5.29E+11 3.25E-07 - 4.14E-07 3.97E+08 4.70E+11 4.14E-07 - 8.00E-07 1.72E+09 2.04E+12 8.00E-07 - 1.00E-06 8.93E+08 1.06E+12 1.00E-06 - 1.13E-06 5.59E+08 6.62E+11 1.13E-06 - 1.30E-06 7.80E+08 9.23E+11 1.30E-06 - 1.86E-06 2.48E+09 2.94E+12 1.86E-06 - 3.06E-06 5.37E+09 6.36E+12 3.06E-06 - 1.07E-05 3.40E+10 4.03E+13 1.07E-05 - 2.90E-05 8.19E+10 9.70E+13 2.90E-05 - 1.01E-04 3.23E+11 3.82E+14 1.01E-04 - 5.83E-04 2.15E+12 2.55E+15 5.83E-04 - 3.04E-03 1.10E+13 1.30E+16 3.04E-03 - 1.50E-02 5.72E+13 6.78E+16 1.50E-02 - 1.11E-01 4.69E+14 5.55E+17 1.11E-01 - 4.08E-01 1.15E+15 1.36E+18 4.08E-01 - 9.07E-01 7.85E+14 9.29E+17 9.07E-01 - 1.42E+00 1.70E+14 2.02E+17 1.42E+00 - 1.83E+00 2.36E+13 2.79E+16 1.83E+00 - 3.01E+00 9.15E+12 1.08E+16 3.01E+00 - 6.38E+00 1.48E+12 1.76E+15 6.38E+00 + 3.94E+07 4.66E+10 Total 2.68E+15 3.168E+18 2 12.2-51 Revision 4

Component (Quantity) Material ter (4) Rh-103 al wire (4) Inconel 600 ation (1) Al2O3 r sheath (1) Inconel 600 r sheath (6) Inconel 600 mocouple: type K chromel-alumel (2) Chromel Alumel meter Value ber of irradiation cycles 1-30 ron flux 2.30E+14 n/cm2-sec 2 12.2-52 Revision 4

In-Core Instrumentation - Gamma Spectra (gamma/sec/assembly)

Energy Group Energy Boundaries (MeV) Cycle 1 Cycle 30 Discharge 3 Day Decay 1 2.00E 3.50E-02 2.06E+13 1.57E+11 2 3.50E 5.00E-02 9.86E+12 8.17E+10 3 5.00E 7.50E-02 1.22E+13 7.01E+10 4 7.50E 1.25E-01 1.14E+13 2.45E+11 5 1.25E 1.75E-01 4.27E+12 4.62E+10 6 1.75E 2.50E-01 3.70E+12 3.65E+10 7 2.50E 4.00E-01 6.22E+12 4.73E+11 8 4.00E 9.00E-01 3.20E+13 9.49E+12 9 9.00E 1.35E+00 2.88E+12 1.13E+13 10 1.35E+00 - 1.80E+00 2.68E+12 3.75E+10 11 1.80E+00 - 2.20E+00 3.31E+12 3.79E+08 12 2.20E+00 - 2.60E+00 1.27E+11 4.54E+06 13 2.60E+00 - 3.00E+00 1.18E+11 1.44E+08 14 3.00E+00 - 3.50E+00 2.10E+10 6.72E+06 15 3.50E+00 - 4.00E+00 9.09E+06 1.98E+05 16 4.00E+00 - 4.50E+00 2.59E+06 1.17E+03 17 4.50E+00 - 5.00E+00 9.23E+05 -

18 5.00E+00 - 1.00E+01 4.31E+08 -

2 12.2-53 Revision 4

Table 12.2-25: Control Rod Assembly Tip Source Term Input Assumptions Parameter Value ron flux at control rod tip 1.40E+12 n/cm2-sec tip irradiation duration 2 cycles CRA Component Material rber Ag-In-Cd k support X-750 ding 304 SS 2 12.2-54 Revision 4

Table 12.2-26: Control Rod Assembly Tip Gamma Spectra (End of Cycle 2)

Discharge 3 Day Decay 30 Day Decay Group Elow (MeV) Ehigh (MeV)

(/sec/kg) (/sec/kg) (/sec/kg) 1 2.00E-02 3.50E-02 2.08E+13 1.61E+11 1.23E+11 2 3.50E-02 5.00E-02 1.18E+13 3.10E+10 2.52E+10 3 5.00E-02 7.50E-02 1.11E+13 2.92E+10 2.37E+10 4 7.50E-02 1.25E-01 1.31E+13 3.08E+10 2.49E+10 5 1.25E-01 1.75E-01 5.99E+12 1.27E+10 1.03E+10 6 1.75E-01 2.50E-01 4.60E+12 3.84E+10 2.83E+10 7 2.50E-01 4.00E-01 7.01E+12 3.45E+10 1.87E+10 8 4.00E-01 9.00E-01 2.64E+13 1.02E+13 9.47E+12 9 9.00E-01 1.35E+00 3.81E+13 1.09E+12 1.01E+12 10 1.35E+00 1.80E+00 4.49E+12 1.47E+12 1.37E+12 11 1.80E+00 2.20E+00 3.78E+12 6.71E+08 6.01E+08 12 2.20E+00 2.60E+00 2.03E+10 2.77E+06 2.57E+06 13 2.60E+00 3.00E+00 1.85E+09 2.07E+05 6.72E+04 14 3.00E+00 3.50E+00 2.21E+08 1.98E+04 1.49E+04 15 3.50E+00 4.00E+00 3.23E+04 3.67E+02 2.12E+02 16 4.00E+00 4.50E+00 4.25E+03 1.05E+00 1.04E-13 17 4.50E+00 5.00E+00 5.40E+00 - -

18 5.00E+00 1.00E+01 3.64E+00 - -

2 12.2-55 Revision 4

Table 12.2-27: Secondary Neutron Source Gamma Spectra (End of Cycle 1)

Discharge 3 Day Decay 30 Day Decay Group Elow (MeV) Ehigh (MeV) Eavg (MeV)

(/sec/assy) (/sec/assy) (/sec/assy) 1 2.00E-02 3.50E-02 2.75E-02 2.11E+15 9.11E+14 3.09E+14 2 3.50E-02 5.00E-02 4.25E-02 7.45E+14 4.12E+14 1.32E+14 3 5.00E-02 7.50E-02 6.25E-02 1.13E+15 3.75E+14 1.18E+14 4 7.50E-02 1.25E-01 1.00E-01 8.10E+14 4.17E+14 1.31E+14 5 1.25E-01 1.75E-01 1.50E-01 3.50E+14 2.18E+14 1.03E+14 6 1.75E-01 2.50E-01 2.13E-01 2.38E+14 1.29E+14 4.13E+13 7 2.50E-01 4.00E-01 3.25E-01 3.42E+14 1.96E+14 7.10E+13 8 4.00E-01 9.00E-01 6.50E-01 1.44E+16 9.74E+15 4.78E+15 9 9.00E-01 1.35E+00 1.13E+00 6.19E+14 5.04E+14 3.26E+14 10 1.35E+00 1.80E+00 1.58E+00 3.35E+15 3.16E+15 2.32E+15 11 1.80E+00 2.20E+00 2.00E+00 4.82E+14 3.38E+14 2.47E+14 12 2.20E+00 2.60E+00 2.40E+00 7.56E+12 2.32E+12 1.70E+12 13 2.60E+00 3.00E+00 2.80E+00 4.96E+12 3.30E+11 2.41E+11 14 3.00E+00 3.50E+00 3.25E+00 8.48E+11 2.28E+07 1.71E+07 15 3.50E+00 4.00E+00 3.75E+00 5.36E+09 4.00E+05 2.44E+05 16 4.00E+00 4.50E+00 4.25E+00 1.96E+09 9.77E+02 9.62E-11 17 4.50E+00 5.00E+00 4.75E+00 1.87E+09 - -

18 5.00E+00 1.00E+01 7.50E+00 3.97E+09 - -

2 12.2-56 Revision 4

Parameter Value ainment release delay 0 hours0 days <br />0 hours <br />0 weeks <br />0 months <br /> ainment release duration 1.0E-05 hours ainment leak rate 0.2%/day ainment 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 sol fraction of non-noble gases released 100%

hield envelope volume 6475 ft3 ary coolant water density 43.6 lb/ft3 ensity 0.07 lb/ft3 ainment air volume 3635 ft3 bined water volume 2500 ft3 2 12.2-57 Revision 4

2 12.2-58 Revision 4 2 12.2-59 Revision 4 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 /> 2.73E+03 36 hour4.166667e-4 days <br />0.01 hours <br />5.952381e-5 weeks <br />1.3698e-5 months <br /> 2.99E+04 3 day 4.01E+04 30 day 9.15E+04 100 day 1.17E+05 Containment vessel Air 1 hour1.157407e-5 days <br />2.777778e-4 hours <br />1.653439e-6 weeks <br />3.805e-7 months <br /> 1.19E+06 36 hour4.166667e-4 days <br />0.01 hours <br />5.952381e-5 weeks <br />1.3698e-5 months <br /> 1.35E+07 3 day 1.84E+07 30 day 4.85E+07 100 day 7.78E+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 /> 7.35E+03 36 hour4.166667e-4 days <br />0.01 hours <br />5.952381e-5 weeks <br />1.3698e-5 months <br /> 8.02E+04 3 day 1.11E+05 30 day 4.30E+05 100 day 1.30E+06 2 12.2-60 Revision 4

Parameter Value ary coolant leak rate 160 lb/day/unit fraction of primary coolant leaks 40%

release from primary coolant leaks 100%

tion coefficients for evaporation and leaks:

ble gases and tritium 1 logens 100 rticulates 200 ines (pool evaporation only) 2000 ary coolant source term Table 11.1-4 Table 11.1-8 water source term Table 12.2-9 Table 12.2-10 Table 12.2-11 evaporation rate: 1705 lb/hour ol surface water temperature 100°F ea of pool water surface 11,845 ft2 velocity over water surface 30 ft/min om air temperature om air relative humidity 85°F 60%

S pump/valve room leak 4 lb/day asifier room leak 13 lb/day mal ventilation air change rates in RXB:

ol air space (100 elevation) 1 air-change/hour CS pump/valve rooms (35-8 elevation) 2 air-changes/hour gasifier rooms (24 elevation) 2 air-changes/hour air space volume 4.42E+10 ml S pump/valve room volume 1.12E+08 ml asifier room volume 3.52E+08 ml 2 12.2-61 Revision 4

Radionuclide CVCS Pump / Valve Room Degasifier Room Air Space above Reactor Pool (Ci/ml) (Ci/ml) (Ci/ml)

Noble Gases Kr83m 1.49E-09 1.49E-09 1.07E-13 Kr85m 6.92E-09 6.92E-09 -

Kr85 2.21E-06 2.21E-06 -

Kr87 3.20E-09 3.20E-09 -

Kr88 1.06E-08 1.06E-08 -

Xe131m 2.86E-08 2.86E-08 1.52E-08 Xe133m 2.61E-08 2.61E-08 2.36E-08 Xe133 1.95E-06 1.95E-06 3.35E-07 Xe135m 1.07E-09 1.07E-09 6.21E-09 Xe135 6.37E-08 6.37E-08 3.45E-09 Xe138 1.20E-09 1.20E-09 -

Halogens Br82 1.95E-13 1.95E-13 2.01E-16 Br83 9.82E-13 9.82E-13 -

Br84 3.16E-13 3.16E-13 -

I129 4.86E-18 4.86E-18 1.23E-20 I130 1.54E-12 1.54E-12 3.04E-16 I131 4.07E-11 4.07E-11 8.73E-12 I132 1.64E-11 1.64E-11 2.19E-14 I133 6.05E-11 6.05E-11 1.01E-12 I134 7.89E-12 7.89E-12 -

I135 3.68E-11 3.68E-11 7.67E-16 Cs, Rb Rb86 1.39E-13 1.39E-13 1.28E-14 Rb88 5.71E-09 5.71E-09 -

Rb89 2.11E-11 2.11E-11 -

Cs132 2.67E-15 2.67E-15 2.16E-16 Cs134 2.40E-11 2.40E-11 2.37E-12 Cs135m 1.30E-14 1.30E-14 -

Cs136 5.08E-12 5.08E-12 4.56E-13 Cs137 1.47E-11 1.47E-11 1.46E-12 Cs138 4.66E-10 4.66E-10 -

Other FP P32 3.97E-19 3.97E-19 1.85E-20 Co57 2.96E-21 2.96E-21 -

Sr89 2.37E-14 2.37E-14 8.94E-16 Sr90 3.98E-15 3.98E-15 2.04E-16 Sr91 8.88E-15 8.88E-15 1.72E-17 Sr92 4.35E-15 4.35E-15 -

Y90 9.82E-16 9.82E-16 1.10E-16 Y91m 5.00E-15 5.00E-15 1.10E-17 Y91 2.57E-15 2.57E-15 1.30E-16 Y92 4.19E-15 4.19E-15 1.17E-19 Y93 1.90E-15 1.90E-15 4.39E-18 2 12.2-62 Revision 4

Radionuclide CVCS Pump / Valve Room Degasifier Room Air Space above Reactor Pool (Ci/ml) (Ci/ml) (Ci/ml)

Zr97 2.83E-15 2.83E-15 2.20E-17 Nb95 4.20E-15 4.20E-15 8.78E-14 Mo99 5.16E-12 5.16E-12 1.64E-13 Mo101 8.08E-14 8.08E-14 -

Tc99m 4.79E-12 4.79E-12 1.58E-13 Tc99 1.49E-16 1.49E-16 7.60E-18 Ru103 4.96E-15 4.96E-15 2.46E-16 Ru105 1.51E-15 1.51E-15 6.42E-20 Ru106 3.22E-15 3.22E-15 1.64E-16 Rh103m 4.90E-15 4.90E-15 2.43E-16 Rh105 3.45E-15 3.45E-15 7.69E-17 Sb124 7.31E-18 7.31E-18 3.66E-19 Sb125 6.44E-17 6.44E-17 3.29E-18 Sb127 2.78E-16 2.78E-16 1.01E-17 Sb129 3.18E-16 3.18E-16 1.27E-20 Te125m 9.46E-15 9.46E-15 4.73E-16 Te127m 3.05E-14 3.05E-14 1.54E-15 Te127 1.18E-13 1.18E-13 1.67E-15 Te129m 8.73E-14 8.73E-14 4.30E-15 Te129 1.08E-13 1.08E-13 2.71E-15 Te131m 2.82E-13 2.82E-13 5.05E-15 Te131 1.05E-13 1.05E-13 1.14E-15 Te132 2.07E-12 2.07E-12 7.03E-14 Te133m 1.29E-13 1.29E-13 -

Te134 1.68E-13 1.68E-13 -

Ba139 3.75E-15 3.75E-15 -

Ba140 2.56E-14 2.56E-14 1.18E-15 La140 7.58E-15 7.58E-15 8.48E-16 La141 1.34E-15 1.34E-15 2.22E-20 La142 5.66E-16 5.66E-16 -

Ce141 3.94E-15 3.94E-15 1.94E-16 Ce143 2.95E-15 2.95E-15 5.82E-17 Ce144 3.31E-15 3.31E-15 1.69E-16 Pr143 3.50E-15 3.50E-15 1.72E-16 Pr144 3.28E-15 3.28E-15 1.67E-16 Np239 6.22E-14 6.22E-14 1.82E-15 Crud Na24 6.42E-12 6.42E-12 3.99E-14 Cr51 3.74E-13 3.74E-13 1.83E-11 Mn54 1.93E-13 1.93E-13 9.81E-12 Fe55 1.44E-13 1.44E-13 7.37E-12 Fe59 3.61E-14 3.61E-14 1.79E-12 Co58 5.54E-13 5.54E-13 2.78E-10 Co60 6.37E-14 6.37E-14 3.26E-12 Ni63 3.18E-14 3.18E-14 1.63E-12 Zn65 6.13E-14 6.13E-14 3.12E-12 2 12.2-63 Revision 4

Radionuclide CVCS Pump / Valve Room Degasifier Room Air Space above Reactor Pool (Ci/ml) (Ci/ml) (Ci/ml)

Zr95 4.69E-14 4.69E-14 2.35E-12 Ag110m 1.56E-13 1.56E-13 7.97E-12 W187 3.30E-13 3.30E-13 4.48E-12 Water Activation Products H3 4.04E-07 4.04E-07 1.46E-06 C14 3.21E-11 3.21E-11 6.34E-12 Ar41 6.28E-08 6.28E-08 -

Assumes the plant consists of 12 NPMs operating on a two-year refueling cycle.

2 12.2-64 Revision 4

Isotope RCS Peak Concentration (Ci/g)

Kr-83m 2.69E+00 Kr-85m 2.14E-01 Kr-85 3.73E+01 Kr-87 6.52E-02 Kr-88 1.90E-01 Xe-131m 1.87E+00 Xe-133m 5.47E+00 Xe-133 2.07E+02 Xe-135m 1.73E+01 Xe-135 1.05E+02 Xe-137 1.39E-02 Xe-138 4.77E-02 Br-82 5.67E-01 Br-83 2.67E+00 Br-84 9.06E-01 Br-85 9.52E-02 I-130 4.45E+00 I-131 1.20E+02 I-132 4.60E+01 I-133 1.75E+02 I-134 2.09E+01 I-135 1.04E+02 Rb-88 3.31E-01 Rb-89 1.08E-02 Cs-134 1.84E-01 Cs-136 3.86E-02 Cs-137 1.27E-01 Cs-138 9.98E-02 Ni-63 4.41E-02 Sr-89 1.10E-02 Zr-95 6.51E-02 Nb-95 6.44E-02 Mo-99 3.88E-02 Tc-99m 7.01E-02 Ag-110m 2.17E-01 Te-132 1.56E-02 Ba-137m 2.26E-01 Na-24 9.11E+00 Cr-51 5.19E-01 Mn-54 2.67E-01 Fe-55 2.00E-01 Fe-59 5.01E-02 Co-58 7.68E+00 Co-60 8.83E-02 W-187 4.65E-01 Zn-65 8.50E-02 2 12.2-65 Revision 4

Isotope RCS Peak Concentration (Ci/g)

H-3 9.90E-01 Ar-41 2.07E-01 2 12.2-66 Revision 4

Radiation protection design features incorporated into the design of the NuScale Power Plant facilities are described in this section. These include features to reduce both onsite and offsite exposures, and to protect the environment. These design features are incorporated into the facility 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 Power Plant design. These design features are incorporated during the design process and the application of industry 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 Radiation sources from sedimentation in tanks are reduced by using tanks with bottoms that slope toward outlets and, where practicable, providing built-in spray features, spargers and eductors for mixing tank contents.

The tanks in the liquid radioactive waste and solid radioactive waste systems are stainless-steel with sloped bottoms. The liquid radioactive waste 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.

Tanks that store spent resins have break pot tanks in the vent line to prevent the tank contents from contaminating the ventilation system.

The pool surge control system (PSCS) storage tank is located in a steel-lined catch basin with sufficient capacity to contain the tank volume along with its associated piping, with a weather enclosure to prevent precipitation from mixing with potentially contaminated fluids.

2 12.3-1 Revision 4

Remotely actuated valves are used to minimize personnel exposures, where practical. 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 solid radioactive waste system (SRWS) and the pool cleanup system (PCUS) 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 high radiation areas, in some applications.

Where possible, 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 For the liquid radioactive waste system (LRWS), piping is seamless stainless steel with large radius bends and butt welded to minimize crud traps. Piping used for slurry transfers associated with the solid radioactive waste system (SRWS) is also butt welded stainless steel pipe with five-diameter bends.

The LRWS and SRWS piping is provided with clean-in-place (CIP) and flushing capabilities to reduce the buildup of crud and other contaminates. The chemical and volume control system (CVCS) and the PCUS 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 practical. Whenever possible, 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 PSCS piping, are enclosed within structured pipe chases or are double-walled. Chemical and volume control system, PSS, and resin sluice pipes that are expected to contain highly contaminated fluids are routed through shielded pipe chases, as much as practical.

2 12.3-2 Revision 4

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

The LRWS uses double diaphragm pumps to reduce leakage and minimize repair times.

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 prior to 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 possible, heat exchangers are designed such that the contaminated fluid is on the tube side.

3.1.1.6 Instrumentation Whenever practical, 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 dampers. Condensate from heating ventilation and air conditioning (HVAC) equipment is routed to the RWDS. Exhaust duct air is exhausted from areas where low levels of airborne 2 12.3-3 Revision 4

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 to prevent blowback in the event of an exhaust system trip.

More discussion on ventilation systems is provided in Section 12.3.3.

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 The filter design used 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 prior to 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.

Demineralizers are designed and constructed to minimize internal crevices and crud traps.

2 12.3-4 Revision 4

The redundant series of charcoal beds of the gaseous radioactive waste system are located in individual shielded cubicles.

The removal of activated charcoal from charcoal beds is done remotely to minimize the occupational exposures to plant personnel.

Radiation detectors monitor each charcoal bed cubicle for gas leaks.

3.1.1.12 Sample Stations Radiation protection design features are incorporated into the design of sample stations for radioactive fluid. Radioactive 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 radioactive fluid is achieved by routing sample lines in shielded pipe chases to the extent practical and locating sample coolers behind the concrete and steel partition wall as necessary. 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 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 steam generator tubing due to 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 coolant or the reactor pool water). Radioactive waste system components are largely designed using stainless steel also, following the recommendations of RG 1.143.

2 12.3-5 Revision 4

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 CRA hub connection couplings (Haynes Alloy-25). The cobalt content of austenitic stainless steel and Ni-Cr-Fe weld filler metals is limited to a maximum of 0.05 percent. The cobalt content of austenitic stainless steel base materials is limited to 0.15 percent.

Steam generator (SG) heat transfer tubing is limited to a cobalt content of a maximum average of 0.014 percent, with zero heats exceeding 0.020 percent.

Table 12.3-4 summarizes the typical cobalt content for materials and components.

3.1.2 Plant and Layout Design Features for ALARA 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 possible.

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 will be sufficiently compensated to comply with the associated radiation zone map dose rates for normally accessible areas.

3.1.2.4 Equipment Layout Radioactive system components are located separately from "clean" components as much as practical. Individual components of a radioactive system are typically 2 12.3-6 Revision 4

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 NuScale Power Plant is analyzed for expected radiation levels resulting from normal operation. Since 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.

Normal operation radiation zones for the RXB are provided in Figure 12.3-1a through Figure 12.3-1i. Areas that have the potential for airborne radiation in the RXB and the Radioactive Waste Building (RWB) are listed in Table 12.3-5a and Table 12.3-5b, respectively. Normal operation radiation zones for the RWB are provided in Figure 12.3-2a and Figure 12.3-2b. These 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 (RCA) 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 is controlled through a portal located in the Annex Building. Radiological areas are posted with signage in compliance with 10 CFR 20.1901 and 20.1902.

High radiation areas either are locked or have alarmed barriers. For areas that are not within lockable enclosures or other barriers, the area will be barricaded and posted, and be provided with a visible warning light. Positive control is exercised 2 12.3-7 Revision 4

Item 12.3-1: A COL applicant that references the NuScale Power Plant design certification 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.

The locations of very high-radiation areas are listed on Table 12.3-3.

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

Item 12.3-3: A COL applicant that references the NuScale Power Plant design certification 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 12.4.1.8 and equipment qualification is addressed in Section 12.2.1.13 and Section 3.11. A radiation and shielding design review has been 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 prior to area entry.

See Section 7.1 for 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. Dose is limited to protect plant personnel, members of the public, and susceptible equipment subject to environmental qualification requirements.

Shielding performance is in accordance with the following criteria:

• ALARA radiation protection principles of 10 CFR 20

• exposure limits of 10 CFR 20 2 12.3-8 Revision 4

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.

The radiation zone maps described in Section 12.3.1 indicate the radiation levels for plant areas.

As described in Section 12.3.1, shielding design features include permanent shielding and separation of components that constitute substantial radiation sources, the use of shielded cubicles, labyrinths, and shielded entrances to minimize dose. 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 ANSI/ANS 6.4-2006 (Reference 12.3-1). Table 12.3-6 and Table 12.3-7 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.

For shield walls that contain a door, the door provides an equivalent radiation attenuation as the shield wall that contains the door. A listing of radiation shield doors is provided in Table 12.3-8 for the RXB and Table 12.3-9 for the RWB.

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 used 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 a Monte Carlo radiation transport code 2 12.3-9 Revision 4

6.1.1-1977, Gamma Flux to Dose Conversion Factors, (Reference 12.3-3) is used to convert gamma flux at each detector location to a corresponding dose rate.

Radioactive components in the RXB and RWB are modeled using MCNP6. The codes used to prepare source strength input data are described in Section 12.2. 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 which incorporate the full volume of the component.

Shielding credit and material selections for MCNP6 cells are conservatively applied. The material compositions for air, concrete, water, and stainless steel are taken from PNNL-25870 (Reference 12.3-4). Structural steel composition is in accordance with plant drawings and ASTM standards. Credit is not taken for reinforcing steel bars in the concrete.

The operating NuScale Power Module (NPM) dose rate at full power is also calculated using MCNP6. The reactor shielding calculations consider dose rates from fission neutrons, fission photons, and gamma output from buildup of radioisotopes in the reactor coolant. The NPM model is conservatively developed using methods similar to the building evaluations. The NPM model determines dose rates for components located below the bioshield.

The fission neutron and fission photon output is based on a total power output of 160 MWt and energy spectrums are based on MCNP6 and SCALE6.1 (Reference 12.3-11) fission neutron and fission gamma distributions. 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. Figure 12.3-3 shows the homogenized regions and the general arrangement of the NPM shielding model.

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 (see Figure 12.3-1a though Figure 12.3-1i).

Radiation zones are selected to facilitate personnel access for operation and maintenance.

3.2.4 Major Component Shielding Design Description 3.2.4.1 NuScale Power Module An NPM is a self-contained nuclear steam supply system composed of a reactor core, a pressurizer, two steam generators integrated within the reactor pressure vessel, CRDMs and valves, and is housed in a compact steel containment vessel.

The containment vessel is partially immersed in the reactor pool as shown in Figure 1.2-5.

2 12.3-10 Revision 4

high-density polyethelene (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 containment vessel, 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.

Item 12.3-8: A COL applicant that references the NuScale Power Plant design certification will describe the radiation shielding design measures used to compensate for major shield wall penetrations in accordance with FSAR Section 12.1.2.3.2 "Minimizing Radiation Levels in Plant Access Areas and Vicinity of Equipment,"

Section 12.3.1.2.3 "Penetrations," and Section 12.3.2.2 "Design Considerations."

Penetration compensatory measures will account for the protection of equipment, and exposures to workers and the public.

3.2.4.2 Main Control Room The dose rate in the main control room 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 15.0-12, 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 12.3-1a through Figure 12.3-1i).

The RXB includes systems that contain radioactive components. The major radiation sources in the RXB are associated with the NPM (see Section 12.3.2.4.1),

chemical volume and control system, PCUS, and spent fuel storage. The shielding designs for these systems are described below.

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 regenerative and non-regenerative heat exchangers are located at elevation 50'-0". The module heatup system heat exchangers are located 2 12.3-11 Revision 4

not required for normal operation of this equipment.

The filters, ion exchangers, and heat exchangers are located in shielded cubicles with knockout panels, which provide equivalent shielding as the wall in which they are located. The CVCS filters and resin traps are accessible via removable floor shield plugs at elevation 35'-8" for maintenance purposes. The cubicle walls are concrete supported by carbon steel plates, called structural steel partition walls.

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 ion exchanger spectra. 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 RCS discharge lines, which travel from the modules to the CVCS heat exchangers and purification equipment through a concrete-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.

Pool Cooling and Cleanup Systems The pool cooling and cleanup systems, which include the spent fuel cooling system, reactor pool cooling system, and the PCUS are located below grade in the RXB. The PCUS demineralizers and filters are located at elevation 24'-0".

The PCUS demineralizers and filters are located in shielded cubicles. The dose rates in surrounding areas are acceptable for operations or maintenance activities. The filters are changed in accordance with ALARA principles to minimize personnel exposure.

For purposes of radiation shielding, the spent fuel pool cooling and reactor pool cooling heat exchangers are a negligible 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 degasifiers and their transfer pumps (both liquid and gaseous) are located within shielded cubicles in the RXB at elevation 24'-0". The degasifier contributes minor dose rates to the adjacent labyrinth and surrounding corridors and is acceptable for operations and maintenance activities.

2 12.3-12 Revision 4

The ultimate heat sink (UHS) is a safety-related pool of borated water that consists of the combined water volume of the reactor pool, refueling pool, 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 storage racks and the refueling pool 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 fuel storage racks in the spent fuel pool, as described in Section 9.1. Due to the depth of water above the stored fuel, the dose rate at the water's surface from the stored fuel is negligible. Likewise, 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 acceptably small.

3.2.4.4 Radioactive Waste Building The RWB houses significant radiation sources that belong to the radioactive waste processing systems. The specifics of these systems are discussed below. The radiation zone maps are located in Figure 12.3-2a and Figure 12.3-2b.

Liquid Radioactive Waste System The LRWS is primarily located in the RWB. The low-conductivity waste (LCW) and high-conductivity waste (HCW) sample tanks (two of each) contain liquid radioactive waste 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 at elevation 71'-0". The respective transfer pumps for these tanks are located in shared compartments in the RWB at elevation 71'-0". 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 other LRWS components that are important radiation sources are located in the RWB at elevation 100'-0". Liquid radioactive waste demineralizers and some of the filters 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, GAC filters, and drum dryer, as noted in Table 12.3-7.

Gaseous Radioactive Waste System The GRWS system is located in the RWB at elevation 71'-0". GRWS components are generally located in separate, shielded compartments.

2 12.3-13 Revision 4

protected by a single guard bed that is in a separately shielded compartment located in the RWB at elevation 71'-0".

The remaining GRW 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 at elevation 71'-0".

Solid Radioactive Waste System The SRWS is located in the RWB at elevations elevation 71'-0" and elevation 100'-0".

SRW 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 at elevation 71'-0". The respective transfer pumps for these tanks are located in shared compartments in the RWB at elevation 71'-0". 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 SRW consists of both Class A and Class B/C waste storage areas. A Class A waste package storage area is located at elevation 100'-0". The Class A high integrity container (HIC) and Class B/C HIC storage area is located at elevation 71'-0". Access to the HIC storage area is through floor shield plugs at elevation 100'-0".

Additional shielding is modeled for the HIC process shield, as noted in Table 12.3-7.

3.3 Ventilation The plant heating, ventilating, and air-conditioning systems are designed to provide a controlled environment for personnel and equipment during normal operation. In areas subject to airborne activity, the ventilation systems are designed to collect, process, and exhaust airborne radioactive material, including directing airflow to processed exhausts (Section 9.4.) This section discusses the radiation control considerations of the HVAC systems design.

3.3.1 Design Objectives Design objectives for the plant heating ventilation and air conditioning systems include the following:

• During normal plant operations, the airborne radioactivity levels to which plant personnel are exposed in radiation controlled areas are maintained ALARA 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.

2 12.3-14 Revision 4

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

Other design features that are incorporated to 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 heating ventilation and air conditioning system is designed to allow rapid replacement of components.

Filter-adsorber unit conformance 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 RXB is normally 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 HEPA filters and charcoal adsorbers. See Section 9.4.2 for additional details.

The dry dock area is provided with exhaust flow to entrain airborne contamination that may result from NPM components being exposed to air during maintenance activities.

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

In response to a high-radiation signal from the spent fuel exhaust ductwork, the RBVS will change into its high-radiological mode. In this mode, the spent fuel pool exhaust flow is diverted through both the HEPA filters and charcoal adsorbers. The general exhaust fans will reduce capacity and maintain the design exhaust airflows for the RWB and Annex Building. The RBVS supply will also reduce its capacity to provide ventilation air while maintaining a negative pressure in the RXB.

2 12.3-15 Revision 4

In addition, the filter units are designed with 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 and is exhausted through the RBVS exhaust system. The main supply air handling unit contains both low and high efficiency outside air filters, a heating coil, and a chilled water cooling coil. Supply air from the main RWBVS is distributed throughout the RWB. Exhaust air is collected and conveyed to the RBVS general exhaust filter units 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. See Section 9.4.3 for 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 has been filtered (low and high efficiency) to maintain a suitable environment for personnel and equipment. The CRVS is designed to maintain a positive pressure inside the main control room (MCR) with respect to adjacent spaces. See Section 9.4.1 for 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 additional HEPA and charcoal filtration. Areas served by the CRVS (MCR and technical support center) are designed to maintain operator doses within PDC 19 limits.

If power is not available, or if a high radiation indication is received from the radiation monitors downstream of the CRVS filter unit, the control room envelope (CRE) isolation dampers close and the control room habitability system is initiated.

3.3.6 Control Room Habitability System The control room habitability system uses a set of compressed air storage tanks to supply the CRE in case of an emergency. Upon receiving an initiation signal, the control room habitability system supplies the MCR control room envelope with clean air and maintains the CRE at a positive pressure with respect to adjacent areas. See Section 6.4 for additional details.

3.4 Area Radiation and Airborne Radioactivity Monitoring Instrumentation The following instrumentation is provided to monitor area radiation and airborne radioactivity within the facility.

2 12.3-16 Revision 4

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 are used to detect fuel cladding breach under potential core damaging accident conditions. The use of these monitors is discussed in Section 9.3.2.

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 prior to reaching predetermined thresholds for radiation. The CVCS reactor coolant ARMs are described in Section 11.5.

The ARMs located in the reactor pool area and 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. In addition, a local area radiation monitor 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 continuous air monitor (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.

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 as low as reasonably achievable conforming to 10 CFR 20.1101(b)

• monitor plant areas during normal operations and anticipated operational occurrences such that the worker limits do not exceed the limits specified in 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 2 12.3-17 Revision 4

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 use in the emergency response data system (ERDS), conforming to 10 CFR 50, Appendix E, VI.2(a)

• provide monitoring of containment radiation levels, conforming to 10 CFR 50.34(f)(2)(xvii)

• 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 area radiation monitors 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 prior to 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. This ensures operator and worker awareness of changing radiological conditions that could indicate system leakage or component malfunction, and provides a warning to plant personnel prior to entry into the affected areas. Where appropriate, local visual alarms are provided outside of the monitored area to ensure worker awareness prior to 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).

For the ARMs in general plant locations, alarm setpoints are established to alert plant personnel when radioactivity in a specific location reaches levels that have 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. This ensures personnel working in the vicinity are able to determine easily the status of an area radiation monitor channel when in the vicinity of the local indication devices.

2 12.3-18 Revision 4

ANS-HPSSC-6.8.1-1981, "Location and Design Criteria for Area Radiation Monitoring Systems for Light Water Nuclear Reactors" (Reference 12.3-6). 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 practical, detectors are located to best measure the representative exposure rates within a given area or specified location.

The following criteria were 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 practical to provide easy maintenance access in an unobstructed area.

The fixed area radiation monitor 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 assure 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 provides an on-scale value for the range of the instrumentation selected.

The fixed area radiation monitor 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 Electric Power Research Institute (EPRI) TR-102644 Revision 1, "Calibration of Radiation Monitors at Nuclear Power Plants" (Reference 12.3-7). 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 ARMs is performed to verify the operability of the channel, including alarm functions in accordance with manufacturer's requirements and using the guidance of EPRI TR-104862, Revision 2, "Area and Process Radiation Monitoring 2 12.3-19 Revision 4

power to the monitor.

Selected ARMs support accident condition response and are PAM system variables, as described in Table 12.3-10 and Table 7.1-7. The fixed area radiation monitors 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 are used to detect fuel damage under accident conditions, and are considered PAM system B and C variables. Two 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 497-2002 "Criteria for Accident Monitoring Instrumentation for Nuclear Power Generating Stations" (Reference 12.3-9). 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 497-2002, Section 6.2, Common Cause Failure.

Fixed area radiation monitoring data is capable of being supplied to the NRC Operations Center through the ERDS via a secure direct electronic data link in the event of an emergency. The ERDS connection is discussed in Section 7.2.

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

• Fixed area radiation monitors that are classified as a Type B post-accident monitoring (PAM) variable receive power from the highly reliable DC power system.

• Fixed area radiation monitors that are classified as a Type C PAM variable receive power from the highly reliable DC power system.

• Fixed area radiation monitors that are classified as a Type E PAM variable receive power from the normal DC power system (EDNS).

• Fixed area radiation monitors that are not used for PAM variables receive power from the EDNS.

The quality and safety classification of the fixed area radiation monitors is provided in Table 3.2-1.

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

Table 12.3-12 provides information about the area radiation monitors used including location and design features such as the type of radiation monitored and the 2 12.3-20 Revision 4

Item 12.3-4: A COL applicant that references the NuScale Power Plant design certification 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.

Item 12.3-5: A COL applicant that references the NuScale Power Plant design certification will describe design criteria for locating additional area radiation monitors.

3.4.3 Airborne Radioactivity Monitoring Instrumentation The fixed continuous airborne radiation monitors (CAMs) 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 prior to 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. This ensures operator and worker awareness of changing radiological conditions that could indicate system leakage or component malfunction, and provides a warning to plant personnel prior to entry into the affected areas. Where appropriate, local visual alarms are provided outside of the monitored area to ensure worker awareness prior to 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 support accident condition response and are PAM system variables, as described in Table 12.3-10 and Table 7.1-7. The fixed CAMs used 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 CAMs data are capable of being supplied to the NRC Operations Center through the ERDS via a secure direct electronic data link in the event of an emergency. The ERDS connection is discussed in Section 7.2.

Alarm setpoints are established to alert plant personnel when airborne radioactivity in a specific location reaches levels that have 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.

2 12.3-21 Revision 4

in the vicinity are able to determine easily the status of fixed CAM 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 12.3-10) and RG 8.25. The following criteria were 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 easy maintenance access in an unobstructed area. The electronic controls for the monitors are placed in the lowest dose area practical.

• Proximity of the airflow path that is as close as practical to potential release points.

The range of the fixed CAM is chosen so that the upper end of the scale is high enough to assure 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 12.3-7). 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, "Area and Process Radiation Monitoring System Guide" (Reference 12.3-8). Check sources integral to the monitor are designed to ensure that the source is returned to the non-test mode upon deactivation or loss of power to the monitor.

Electrical power to the fixed CAMs is provided by the following systems

• Fixed continuous airborne radiation monitors that are classified as a Type E PAM variable receive power from the EDNS.

2 12.3-22 Revision 4

The quality and safety classification of the fixed area radiation monitors is provided in Table 3.2-1.

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

Table 12.3-11 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 Item 12.3-6: A COL applicant that references the NuScale Power Plant design certification 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 See Section 12.4.

3.6 Minimization of Contamination and Radioactive Waste Generation Design features incorporated into the NuScale Power 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 was 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 NuScale Power Plant SSC that have the potential to contain contaminated fluids have design features to reduce the likelihood of leaks, have provisions to detect leaks that do occur and reduce the spread of contamination, thus reducing the need for decontamination and the generation of waste. The list of structures and systems in a NuScale Power Plant that have been evaluated for design features consistent with RG 4.21 is provided in Table 12.3-13. The results of the system evaluations are provided in Table 12.3-14 through Table 12.3-44.

3.6.1 Facility Design Objectives for 10 CFR 20.1406 Regulatory Guide 4.21 addresses each phase of the NuScale Power Plant lifecycle, from the early design phases through decommissioning. To address these phases, NuScale has divided the discussion into the following four design objectives and two operational objectives. Application of these six objectives demonstrates compliance with 10 CFR 20.1406 requirements.

2 12.3-23 Revision 4

decommissioning. These measures were developed to 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 are incorporated, as appropriate:

• proper selection of materials that is commensurate with the SSC service conditions to reduce the effects of corrosion, temperature, pressure, etc.

• 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 3.6.1.2 Design Considerations for Leak Detection - Objective 2 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 2 12.3-24 Revision 4

• 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 Certain design considerations can be employed to facilitate the eventual decommission process. The following facility design features are included, as appropriate:

• use of modular construction

• minimize the use of buried or embedded piping and components

• use of removable walls to ease component removal

• 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 2 12.3-25 Revision 4

• 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 to be 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.

Item 12.3-7: A COL applicant that references the NuScale Power Plant design certification 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, Oak Ridge, TN.

12.3-3 American National Standards Institute/American Nuclear Society, "Neutron and Gamma-Ray Flux-to-Dose-Rate Factors," ANSI/ANS 6.1.1-1977, La Grange Park, IL.

12.3-4 Pacific Northwest National Laboratory, "Compendium of Material Composition for Radiation Transport Modeling," PNNL-25870, Rev. 1, March 2011.

12.3-5 American National Standards Institute/American Nuclear Society, "Design Requirement for Light Water Reactor Fuel Handling Systems," ANSI/ANS-57.1-1992, La Grange Park, IL.

2 12.3-26 Revision 4

Nuclear Reactors," ANSI/ANS/HPSSC-6.8.1-1981, LaGrange Park, Il.

12.3-7 Electric Power Research Institute, "Calibration of Radiation Monitors at Nuclear Power Plants," EPRI #102644, Rev. 1, December 2005, Palo Alto, CA.

12.3-8 Electric Power Research Institute, "Area and Process Radiation Monitoring System Guide," EPRI #104862, Rev. 2, August 2003, Palo Alto, CA.

12.3-9 Institute of Electrical and Electronics Engineers, "Criteria for Accident Monitoring Instrumentation for Nuclear Power Generating Stations,"

IEEE Standard 497-2002, New York, NY.

12.3-10 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.

12.3-11 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.

2 12.3-27 Revision 4

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

Controlled Zones I Controlled area Limited 0.05 mrem/hr 0.5 Sv/hr Areas of the plant that can be 10 CFR 20.1502(a)(1) occupancy occupationally occupied without 0.25 mrem/hr 2.5 Sv/hr 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 Sv/hr Areas of the plant that can be 10 CFR 20.1201(a) radiation occupationally occupied without monitoring 2.5 mrem/hr 0.025 mSv/hr 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) access to ensure compliance with the 5 mrem/hr 0.05 mSv/hr 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 radiation areas.

100 mrem/hr 1 mSv/hr V High Radiation area1 Access 100 mrem/hr 1 mSv/hr Areas of the plant that require controlled 10 CFR 20.1601 restriction access and posting as high radiation areas.

1 Rad/hr 10 mGy/hr 10 CFR 20.1902(b)

Radiation Protection Design Features 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 radiation 10 CFR 20.1902(c) 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 zones with tion dose rates above 1 Rad/hr.

cale 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) occupied without personnel radiation monitoring 0.1 DAC 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 occupied without exceeding the airborne 0.3 DAC radioactivity area limit requiring respiratory 10 CFR 20.1502(b)(1) protective equipment.

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

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

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

Room # Description Reactor Building None Radioactive Waste Building EL 71'-0" 030-034 (see Figure 1.2-28) Class A/B/C HIC Room Radioactive Waste Building EL 100'-0" None 2 12.3-30 Revision 4

erial or Application Maximum Weight Percent of Cobalt enitic stainless steel weld filler metals (including cladding) 1 0.05 enitic stainless steel base materials 1 0.15 tor vessel internal core reflector blocks 0.05 r-Fe base metals and weld filler metals1 0.05 ept Alloy 690 SG tubing below) 690 SG tubing 0.014 max average (with zero heat to exceed 0.020) r small components in contact with primary coolant Not limited, however low or zero cobalt materials will be used as available M internals springs in contact with primary coolant (Inconel 1.00 0) 1: For RCS piping, reactor vessel internals (except core reflector blocks), and RPV 2 12.3-31 Revision 4

tion & Room # (see Note 1) Description Source of Airborne Radioactive Material ation 24 west wing (010-007 & 010-008) PCU filter rooms Pool water ation 24 south wing PCU demineralizers and adjacent Pool water, and PCU

-052, 052a; 010-053, 053a, & 010-054) valve galleries demineralizer resin ation 24' northwest corner (010-009 & 010-012) Degasifier Rooms CVCS letdown ation 24' north wing (010-040, 041, 042, 043, 044 & CVCS valve gallery Primary coolant ation 24' south wing (010-046, 047, 048, 049, 050 & CVCS valve gallery Primary coolant ation 35'-8" north wing (010-026, 027, 028, 029, 030 CVCS recirculation pump room Primary coolant 1) ation 35'-8" south wing (010-032, 033, 034, 035, 036 CVCS recirculation pump room Primary coolant 7) ation 50 west wing (010-106) Spent fuel pool cooling area Pool water ation 50 south west side (010-134) Reactor pool cooling area Pool water ation 50 north and south wings (010-114, & 010- Utility areas adjacent to CVCS Leaked airborne from CVCS heat exchanger valve galleries valve galleries ation 50 east wing (010-121) Hot lab Primary coolant samples ation 100 north wing west half (010-409) Containment flood and drain area Pool water ation 100 south wing west half (010-420) Containment flood and drain area Pool water ation 62' north wing (010-139) MHS heat exchanger Primary coolant ation 62' south wing (010-140) MHS heat exchanger Primary coolant ation 100' (010-422 & 423) RXB area above pool Pool water evaporation ation 100 north wing east half (010-411) Hallway with CES Vented RCS leaks into containment vessel ation 100 south wing east half (010-418) Hallway with CES Vented RCS leaks into containment vessel 1: Refer to Figure 1.2-10 through Figure 1.2-18 for room locations.

2 12.3-32 Revision 4

tion & Room # (see Note 1) Description Source of Airborne Radioactive Material ation 71 center SRW resin tanks and transfer Spent resin

-011, 030-012, 030-013, 030-026, 030- pump rooms

& 030-028) ation 71 center LRWS tanks and transfer pumps Liquid radioactive waste

-014 through 030-025) ation 71 south west GRWS vessels and cooler rooms Gaseous radioactive waste

-004, 030-005, & 030-006) ation 71 south west HIC fill station room Spent resin

-033) ation 100 LRW equipment room Liquid radioactive waste

-105) ation 100 LRWS drum dryers Liquid radioactive waste

-106, & 030-107) ation 100 Class A storage and sorting rooms Solid radioactive waste

-111, and 030-112) ation 100 Mechanical Room (RBVS and RBVS and RWBVS Exhaust

-101) RWBVS exhaust systems) 1: Refer to Figure 1.2-28, Figure 1.2-29 and Figure 1.2-30 for room locations.

2 12.3-33 Revision 4

cale Final Safety Analysis Report

v. Room # Room Name North Wall East Wall South Wall West Wall Floor Ceiling Source Term (Note 1) (Note 2) (Note 2) (Note 2) (Note 2) (Note 3) (Note 3) 010-040 Module 1 CVCS 20 Structural 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 10 Concrete 20 Concrete/steel CVCS mixed bed ion exchanger steel partition wall partition wall partition wall partition wall (ground floor) composite slab and CVCS cation sluice room bed 010-041 Module 2 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20Concrete/steel 10 Concrete 20 Concrete/steel CVCS mixed bed ion exchanger partition wall partition wall partition wall partition wall (ground floor) composite slab and CVCS cation sluice room bed 010-042 Module 3 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20Concrete/steel 10 Concrete 20 Concrete/steel CVCS mixed bed ion exchanger partition wall partition wall partition wall partition wall (ground floor) composite slab and CVCS cation sluice room bed 010-043 Module 4 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 10 Concrete 20 Concrete/steel CVCS mixed bed ion exchanger partition wall partition wall partition wall partition wall (ground floor) composite slab and CVCS cation sluice room bed 010-044 Module 5 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 10 Concrete 20 Concrete/steel CVCS mixed bed ion exchanger partition wall partition wall partition wall partition wall (ground floor) composite slab and CVCS cation sluice room bed 010-045 Module 6 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 10 Concrete 20 Concrete/steel CVCS mixed bed ion exchanger partition wall partition wall partition wall partition wall (ground floor) composite slab and CVCS cation sluice room bed 010-051 Module 7 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 10 Concrete 20 Concrete/steel CVCS mixed bed ion exchanger partition wall partition wall partition wall partition wall (ground floor) composite slab and CVCS cation sluice room bed 010-050 Module 8 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 10 Concrete 20 Concrete/steel CVCS mixed bed ion exchanger partition wall partition wall partition wall partition wall (ground floor) composite slab and CVCS cation sluice room bed Radiation Protection Design Features 010-049 Module 9 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20Concrete/steel 10 Concrete 20 Concrete/steel CVCS mixed bed ion exchanger partition wall partition wall partition wall partition wall (ground floor) composite slab and CVCS cation sluice room bed 010-048 Module 10 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 10 Concrete 20 Concrete/steel CVCS mixed bed ion exchanger partition wall partition wall partition wall partition wall (ground floor) composite slab and CVCS cation sluice room bed 010-047 Module 11 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 10 Concrete 20 Concrete/steel CVCS mixed bed ion exchanger partition wall partition wall partition wall partition wall (ground floor) composite slab and CVCS cation sluice room bed

cale Final Safety Analysis Report

v. Room # Room Name North Wall East Wall South Wall West Wall Floor Ceiling Source Term (Note 1) (Note 2) (Note 2) (Note 2) (Note 2) (Note 3) (Note 3) 010-046 Module 12 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 10 Concrete 20 Concrete/steel CVCS mixed bed ion exchanger partition wall partition wall partition wall partition wall (ground floor) composite slab and CVCS cation sluice room bed 010-012 Degasifier room 5 Concrete, RXB 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 10 Concrete 3 Concrete (floor Degasifier A exterior wall partition wall partition wall partition wall (ground floor) of 50 elevation) 010-009 Degasifier room 5 Concrete, RXB 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 10 Concrete 3 Concrete (floor Degasifier B exterior wall partition wall partition wall partition wall (ground floor) of 50 elevation) 010-008 Pool cleanup 5' Concrete, RXB 20 Concrete/steel 20 Concrete/steel 5 concrete, RXB 10 Concrete 3 Concrete (floor The dose rate filter room A wall partition wall partition wall exterior wall (ground floor) of 50 elevation) from the PCU filters is assumed to be 10% of that from a PCU demineralizer.

010-007 Pool cleanup 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 5 concrete, RXB 10 Concrete 3 Concrete (floor The dose rate filter room B partition wall partition wall partition wall exterior wall (ground floor) of 50 elevation) from the PCU filters is assumed to be 10% of that from a PCU demineralizer.

010-052 PCUS demin 20 Concrete/steel 20 Concrete/steel 5 Concrete, RXB 20 Concrete/steel 10 Concrete 3 Concrete (floor PCUS room #1 partition wall partition wall exterior wall partition wall (ground floor) of 50 elevation demineralizer 010-054 PCUS demin 20 Concrete/steel 20 Concrete/steel 5 Concrete, RXB 20 Concrete/steel 10 Concrete 3 Concrete (floor PCUS room #2 partition wall partition wall exterior wall partition wall (ground floor) of 50 elevation demineralizer Radiation Protection Design Features 010-053 PCUS demin 20 Concrete/steel 20Concrete/steel 5 Concrete, RXB 20 Concrete/steel 10 Concrete 3 Concrete (floor PCUS room #3 partition wall partition wall exterior wall partition wall (ground floor) of 50 elevation demineralizer 8 N/A Horizontal Pipe 20 Concrete 20 Concrete 20 Concrete 20 Concrete 20 Concrete 20 Concrete CVCS resin Chase transfer pipe

cale Final Safety Analysis Report

v. Room # Room Name North Wall East Wall South Wall West Wall Floor Ceiling Source Term (Note 1) (Note 2) (Note 2) (Note 2) (Note 2) (Note 3) (Note 3) 8 010-026 Module 1 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 3 Concrete (floor The recirc. pump partition wall partition wall partition wall partition wall composite slab of 50 elevation predominant room radiation source for this area originates from the 24' elevation CVCS ion exchanger room.

8 010-027 Module 2 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 3 Concrete (floor The recirc. pump partition wall partition wall partition wall partition wall composite slab of 50 elevation predominant room radiation source for this area originates from the 24' elevation CVCS ion exchanger room.

8 010-028 Module 3 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20Concrete/steel 20 Concrete/steel 3 Concrete (floor The recirc. pump partition wall partition wall partition wall partition wall composite slab of 50 elevation predominant room radiation source for this area originates from the 24' elevation CVCS ion exchanger Radiation Protection Design Features room.

8 010-029 Module 4 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 3 Concrete (floor The recirc. pump partition wall partition wall partition wall partition wall composite slab of 50 elevation predominant room radiation source for this area originates from the 24' elevation CVCS ion exchanger room.

cale Final Safety Analysis Report

v. Room # Room Name North Wall East Wall South Wall West Wall Floor Ceiling Source Term (Note 1) (Note 2) (Note 2) (Note 2) (Note 2) (Note 3) (Note 3) 8 010-030 Module 5 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 3 Concrete (floor The recirc. pump partition wall partition wall partition wall partition wall composite slab of 50 elevation predominant room radiation source for this area originates from the 24' elevation CVCS ion exchanger room.

8 010-031 Module 6 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 3 Concrete (floor The recirc. pump partition wall partition wall partition wall partition wall composite slab of 50 elevation predominant room radiation source for this area originates from the 24' elevation CVCS ion exchanger room.

8 010-037 Module 7 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 3 Concrete (floor The recirc. pump partition wall partition wall partition wall partition wall composite slab of 50 elevation predominant room radiation source for this area originates from the 24' elevation CVCS ion exchanger Radiation Protection Design Features room.

8 010-036 Module 8 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 3 Concrete (floor The recirc. pump partition wall partition wall partition wall partition wall composite slab of 50 elevation predominant room radiation source for this area originates from the 24' elevation CVCS ion exchanger room.

cale Final Safety Analysis Report

v. Room # Room Name North Wall East Wall South Wall West Wall Floor Ceiling Source Term (Note 1) (Note 2) (Note 2) (Note 2) (Note 2) (Note 3) (Note 3) 8 010-035 Module 9 CVCS 20Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 3 Concrete (floor The recirc. pump partition wall partition wall partition wall partition wall composite slab of 50 elevation predominant room radiation source for this area originates from the 24' elevation CVCS ion exchanger room.

8 010-034 Module 10 CVCS 20Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 3 Concrete (floor The recirc. pump partition wall partition wall partition wall partition wall composite slab of 50 elevation predominant room radiation source for this area originates from the 24' elevation CVCS ion exchanger room.

8 010-033 Module 11 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20Concrete/steel 20 Concrete/steel 3 Concrete (floor The recirc. pump partition wall partition wall partition wall partition wall composite slab of 50 elevation predominant room radiation source for this area originates from the 24' elevation CVCS ion exchanger Radiation Protection Design Features room.

8 010-032 Module 12 CVCS 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 3 Concrete (floor The recirc. pump partition wall partition wall partition wall partition wall composite slab of 50 elevation predominant room radiation source for this area originates from the 24' elevation CVCS ion exchanger room.

cale Final Safety Analysis Report

v. Room # Room Name North Wall East Wall South Wall West Wall Floor Ceiling Source Term (Note 1) (Note 2) (Note 2) (Note 2) (Note 2) (Note 3) (Note 3) 010-115 Module 1 CVCS 20 Concrete/steel 20 Concrete/steel 5 Concrete 20 Concrete/steel 3 Concrete (floor 20 Concrete/steel CVCS heat heat exchanger partition wall partition wall (reactor pool wall) partition wall of 50 elevation) composite slab exchanger room 010-116 Module 2 CVCS 20 Concrete/steel 20 Concrete/steel 5 Concrete 20 Concrete/steel 3 Concrete (floor 20 Concrete/steel CVCS heat heat exchanger partition wall partition wall (reactor pool wall) partition wall of 50 elevation) composite slab exchanger room 010-117 Module 3 CVCS 20 Concrete/steel 20 Concrete/steel 5 Concrete 20 Concrete/steel 3 Concrete (floor 20 Concrete/steel CVCS heat heat exchanger partition wall partition wall (reactor pool wall) partition wall of 50 elevation) composite slab exchanger room 010-118 Module 4 CVCS 20 Concrete/steel 20 Concrete/steel 5 Concrete 20 Concrete/steel 3 Concrete (floor 20 Concrete/steel CVCS heat heat exchanger partition wall partition wall (reactor pool wall) partition wall of 50 elevation) composite slab exchanger room 010-119 Module 5 CVCS 20 Concrete/steel 20 Concrete/steel 5 Concrete 20 Concrete/steel 3 Concrete (floor 20 Concrete/steel CVCS heat heat exchanger partition wall partition wall (reactor pool wall) partition wall of 50 elevation) composite slab exchanger room 010-120 Module 6 CVCS 20 Concrete/steel 20 Concrete/steel 5 Concrete 20 Concrete/steel 3 Concrete (floor 20 Concrete/steel CVCS heat heat exchanger partition wall partition wall (reactor pool wall) partition wall of 50 elevation) composite slab exchanger room 010-126 Module 7 CVCS 5 Concrete 20 Concrete/steel 20 Structural 20Concrete/steel 3 Concrete (floor 20 Structural CVCS heat heat exchanger (reactor pool wall) partition wall steel partition wall partition wall of 50 elevation) steel partition wall exchanger room 010-127 Module 8 CVCS 5 Concrete 20 Concrete/steel 20 Structural 20 Concrete/steel 3 Concrete (floor 20Concrete/steel CVCS heat heat exchanger (reactor pool wall) partition wall steel partition wall partition wall of 50 elevation) composite slab exchanger room 010-128 Module 9 CVCS 5 Concrete 20 Concrete/steel 20 Structural 20Concrete/steel 3 Concrete (floor 20 Concrete/steel CVCS heat Radiation Protection Design Features heat exchanger (reactor pool wall) partition wall steel partition wall partition wall of 50 elevation) composite slab exchanger room 010-129 Module 10 CVCS 5 Concrete 20 Concrete/steel 20 Structural 20 Concrete/steel 3 Concrete (floor 20 Concrete/steel CVCS heat heat exchanger (reactor pool wall) partition wall steel partition wall partition wall of 50 elevation) composite slab exchanger room 010-130 Module 11 CVCS 5 Concrete 20 Concrete/steel 20 Structural 20 Concrete/steel 3 Concrete (floor 20 Concrete/steel CVCS heat heat exchanger (reactor pool wall) partition wall steel partition wall partition wall of 50 elevation) composite slab exchanger room 010-131 Module 12 CVCS 5 Concrete 20 Concrete/steel 20 Structural 20Concrete/steel 3 Concrete (floor 20 Concrete/steel CVCS heat heat exchanger (reactor pool wall) partition wall steel partition wall partition wall of 50 elevation) composite slab exchanger room

cale Final Safety Analysis Report

v. Room # Room Name North Wall East Wall South Wall West Wall Floor Ceiling Source Term (Note 1) (Note 2) (Note 2) (Note 2) (Note 2) (Note 3) (Note 3) 010-106 Vertical pipe 20 Concrete 20 Concrete 20 Concrete 5 Concrete (RXB N/A N/A CVCS pipe chase exterior) 010-139 Modules 1-6 5 Concrete 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 20 Concrete/steel 3 Concrete (floor CVCS heat heatup heat (reactor pool wall) partition wall partition wall partition wall composite slab of 75 elevation) exchanger exchangers 010-140 Modules 7-12 20 Concrete/steel 20 Concrete/steel 5 Concrete 20 Concrete/steel 20 Concrete/steel 3 Concrete (floor CVCS heat heatup heat partition wall partition wall (reactor pool wall) partition wall composite slab of 75 elevation) exchanger exchangers N/A Modules 1-6 20 Concrete 20 Concrete 5 Concrete 20 Concrete N/A N/A CVCS pipe CVCS vertical (reactor pool wall) pipe chases N/A Modules 7-12 5 Concrete 20 Concrete 20 Concrete 20 Concrete N/A N/A CVCS pipe CVCS vertical (reactor pool wall) pipe chases N/A Modules 1-6 20 Concrete 20 Concrete 5 Concrete 20 Concrete N/A N/A CVCS pipe CVCS vertical (reactor pool wall) pipe chases N/A Modules 7-12 5 Concrete 20 Concrete 20 Concrete 20 Concrete N/A N/A CVCS pipe CVCS vertical (reactor pool wall) pipe chases N/A Modules 1-6 20 Concrete 20 Concrete 5 Concrete 20Concrete N/A N/A CVCS pipe CVCS vertical (reactor pool wall) pipe chases N/A Modules 7-12 5 Concrete 20 Concrete 20 Concrete 20Concrete N/A N/A CVCS pipe CVCS vertical (reactor pool wall)

Radiation Protection Design Features pipe chases 6 010-022 Reactor pool 5' Concrete wall, 5' Concrete wall 5' Concrete wall, 5' Concrete wall 23.5" Concrete 4' Concrete roof NPM area 4" HDPE, 5% 4" HDPE, 5% 2 x 0.25" Steel boron content boron content (Bioshield)

(Bioshield vertical (Bioshield vertical portion in front of portion in front of operating bay) operating bay) 1: Refer to Figure 1.2-10 through Figure 1.2-18 for room locations.

2: A 20" concrete/steel partition wall consists of two one-half inch steel plates with 19" of concrete in between.

3: A 20" concrete/steel composite slab consists of two one-half inch steel plates with 19" of concrete in between.

cale Final Safety Analysis Report

v. Room # Room Name North Wall East Wall South Wall West Wall Floor Ceiling Source Term 030-004 Tank Room 20 Concrete 20 Concrete 20 Concrete 48 Concrete 60 Concrete 24 Concrete GRWS Charcoal Beds Wall (Facility (Facility Basemat)

External Wall) 030-005 Tank Room 20 Concrete 20 Concrete 20 Concrete 48 Concrete 60 Concrete 24 Concrete GRWS Charcoal Beds Wall (Facility (Facility Basemat)

External Wall) 030-012 Tank Room 36 Concrete 48 Concrete 15 Concrete 15 Concrete 60 Concrete 24 Concrete Phase Separator Tank Wall (Facility (Facility Basemat)

External Wall) 030-013 Tank Room 36 Concrete 15 Concrete 15 Concrete 24 Concrete 60 Concrete 24 Concrete Phase Separator Tank (Facility Basemat) 030-015 Tank Room 36 Concrete 24 Concrete 24 Concrete 24 Concrete 60 Concrete 24 Concrete HCW Collection Tank (Facility Basemat) 030-016 Tank Room 36 Concrete 24 Concrete 24 Concrete 24 Concrete 60 Concrete 24 Concrete HCW Collection Tank (Facility Basemat) 030-018 Tank Room 24 Concrete 24 Concrete 36 Concrete 24 Concrete 60 Concrete 24 Concrete LCW Collection Tank (Facility Basemat) 030-019 Tank Room 24 Concrete 24 Concrete 36 Concrete 24 Concrete 60 Concrete 24 Concrete LCW Collection Tank (Facility Basemat) 030-020 Tank Room 24 Concrete 24 Concrete 36 Concrete 24 Concrete 60 Concrete 24 Concrete LCW Sample Tank (Facility Basemat) 030-021 Tank Room 24 Concrete 24 Concrete 24 Concrete 24 Concrete 60 Concrete 24 Concrete LCW Sample Tank (Facility Basemat) 030-024 Tank Room 24 Concrete 24 Concrete 24 Concrete 24 Concrete 60 Concrete 24 Concrete HCW Sample Tank Radiation Protection Design Features (Facility Basemat) 030-025 Tank Room 24 Concrete 34 Concrete 24 Concrete 24 Concrete 60 Concrete 24 Concrete HCW Sample Tank (Facility Basemat) 030-026 Tank Room 36 Concrete 34 Concrete 36 Concrete 34 Concrete 60 Concrete 24 Concrete Spent Resin Storage Tank (Facility Basemat) 030-027 Tank Room 36 Concrete 48 Concrete 36 Concrete 34 Concrete 60 Concrete 24 Concrete Spent Resin Storage Tank Wall (Facility (Facility Basemat)

External Wall) 030-033 HIC Filling 36 Concrete 36 Concrete 36 Concrete 36 Concrete 60 Concrete 24 Concrete HIC Room (Note 1) (Note 1) (Note 1) (Note 1) (Facility Basemat)

cale Final Safety Analysis Report

v. Room # Room Name North Wall East Wall South Wall West Wall Floor Ceiling Source Term 030-034 Class A/B/C 36 Concrete 36 Concrete 36 Concrete 48 Concrete 60 Concrete 24 Concrete HIC HIC Room Wall (Facility (Facility Basemat)

External Wall)

--- Pipe Chase 24 Concrete 24 Concrete 24 Concrete 24 Concrete 20 Concrete 24 Concrete Resin transfer pipe 0 030-105 LRW 24 Concrete 36 Concrete 24 Concrete 36 Concrete 24 Concrete 12 Concrete - LCW GAC (vessel steel wall Processing Facility Ceiling thickness = 1.3");

Area (Note 2) LCW TUF (vessel steel wall thickness

= 0.25");

LCW RO (vessel steel wall thickness

= 0.25");

HCW GAC (vessel steel wall thickness = 1.3");

HCW TUF (vessel steel wall thickness = 0.25");

HCW RO (vessel steel wall thickness

= 0.25");

LCW Cation Demineralizer (vessel steel wall thickness = 1.3");

LCW Anion Demineralizer (vessel steel wall thickness = 1.3");

LCW Mixed Bed Demineralizer (vessel steel wall thickness = 0.25");

LCW Cesium Demineralizer (vessel steel wall thickness = 1.3").

Radiation Protection Design Features 0 030-106 Drum Dryer 24 Concrete 12 Concrete 24 Concrete 36 Concrete 24 Concrete 12 Concrete - Drum Dryer Room A Facility Ceiling (Note 3) 0 030-107 Drum Dryer 24 Concrete 36 Concrete 24 Concrete 12 Concrete 24 Concrete 12 Concrete - Drum Dryer Room B Facility Ceiling (Note 3) 1: The equivalent attenuation to an additional 4.5 inches of lead is provided for a HIC process shield.

2: The equivalent attenuation to an additional one inch of steel on top of the LCW demineralizers and GAC processing skids is provided.

3: The equivalent attenuation to an additional two inches of steel on top of the drum dryer skid is provided.

Table 12.3-8: Reactor Building Radiation Shield Doors eactor Reactor Reactor Building Room Name Reactor Reactor Reactor Building Room Name ilding Building Building Building oor # Room #1 Door # Room #1 007A 010-007 Pool Cleanup Filter Rm. B 033B 010-033 Module 11 CVCS Recirc. Pump Room (middle door) 008A 010-008 Pool Cleanup Filter Rm. A 033C 010-033 Module 11 CVCS Recirc. Pump Room (east door) 009A 010-009 Degasifier Room B 034A 010-034 Module 10 CVCS Recirc. Pump Room (west door) 012A 010-012 Degasifier Room A 034B 010-034 Module 10 CVCS Recirc. Pump Room (middle door) 016A Corridor 24 Elevation; North corridor 034C 010-034 Module 10 CVCS Recirc. Pump (southeast door) Room (east door) 016B Corridor 24 Elevation; North corridor 035A 010-035 Module 9 CVCS Recirc. Pump (northeast door) Room (west door) 016C Corridor 24 Elevation; North corridor 035B 010-035 Module 9 CVCS Recirc. Pump (northwest door) Room (middle door) 016D Corridor 24 Elevation; North corridor 035C 010-035 Module 9 CVCS Recirc. Pump (southwest door) Room (east door) 018A Corridor 24 Elevation; South corridor 036A 010-036 Module 8 CVCS Recirc. Pump (northeast door) Room (west door) 018B Corridor 24 Elevation; South corridor 036B 010-036 Module 8 CVCS Recirc. Pump (southeast door) Room (middle door) 018C Corridor 24 Elevation; South corridor 036C 010-036 Module 8 CVCS Recirc. Pump (southwest door) Room (east door) 018D Corridor 24 Elevation; South corridor 037A 010-037 Module 7 CVCS Recirc. Pump (northwest door) Room (west door) 026A 010-026 Module 1 CVCS Recirc. Pump 037B 010-037 Module 7 CVCS Recirc. Pump Room (east door) Room (middle door) 026B 010-026 Module 1 CVCS Recirc. Pump 037C 010-037 Module 7 CVCS Recirc. Pump Room (middle door) Room (east door) 026C 010-026 Module 1 CVCS Recirc. Pump 040A 010-040 Module 1 Ion Exchanger Room Room (west door) 027A 010-027 Module 2 CVCS Recirc. Pump 041A 010-041 Module 2 Ion Exchanger Room Room (east door) 027B 010-027 Module 2 CVCS Recirc. Pump 042A 010-042 Module 3 Ion Exchanger Room Room (middle door) 027C 010-027 Module 2 CVCS Recirc. Pump 043A 010-043 Module 4 Ion Exchanger Room Room (west door) 028A 010-028 Module 3 CVCS Recirc. Pump 044A 010-044 Module 5 Ion Exchanger Room Room (east door) 028B 010-028 Module 3 CVCS Recirc. Pump 045A 010-045 Module 6 Ion Exchanger Room Room (middle door) 028C 010-028 Module 3 CVCS Recirc. Pump 046A 010-046 Module 12 Ion Exchanger Room Room (west door) 029A 010-029 Module 4 CVCS Recirc. Pump 047A 010-047 Module 11 Ion Exchanger Room Room (east door) 029B 010-029 Module 4 CVCS Recirc. Pump 048A 010-048 Module 10 Ion Exchanger Room Room (middle door) 2 12.3-43 Revision 4

eactor Reactor Reactor Building Room Name Reactor Reactor Reactor Building Room Name ilding Building Building Building oor # Room #1 Door # Room #1 029C 010-029 Module 4 CVCS Recirc. Pump 049A 010-049 Module 9 Ion Exchanger Room Room (west door) 030A 010-030 Module 5 CVCS Recirc. Pump 050A 010-050 Module 8 Ion Exchanger Room Room (east door) 030B 010-030 Module 5 CVCS Recirc. Pump 051A 010-051 Module 7 Ion Exchanger Room Room (middle door) 030C 010-030 Module 5 CVCS Recirc. Pump 052A 010-052 PCU Demin Room #1 Room (west door) 031A 010-031 Module 6 CVCS Recirc. Pump 053A 010-053 PCU Demin Room #3 Room (east door) 031B 010-031 Module 6 CVCS Recirc. Pump 114C 010-114 50 Elevation North utilities area Room (middle door) (west door) 031C 010-031 Module 6 CVCS Recirc. Pump 114D 010-114 50 Elevation North utilities area Room (west door) (middle door) 032A 010-032 Module 12 CVCS Recirc. Pump 114E 010-114 50 Elevation North utilities area Room (west door) (east door) 032B 010-032 Module 12 CVCS Recirc. Pump 125C 010-125 50 Elevation South utilities area Room (middle door) (west door) 032C 010-032 Module 12 CVCS Recirc. Pump 125D 010-125 50 Elevation South utilities area Room (east door) (middle door) 033A 010-033 Module 11 CVCS Recirc. Pump 125E 010-125 50 Elevation South utilities area Room (west door) (east door) 1: Refer to Figure 1.2-10, Figure 1.2-11 and Figure 1.2-12 for room locations.

2 12.3-44 Revision 4

ioactive Radioactive Radioactive Waste Building Radioactive Radioactive Radioactive Waste Building Waste Waste Room Name Waste Waste Room Name ilding Building Building Building oor # Room #1 Door # Room #1 020A 030-020 Tank room (82 Elev.) 018A 030-018 Tank room (82 Elev.)

021A 030-021 Tank room (82 Elev.) 016A 030-016 Tank room (82 Elev.)

024A 030-024 Tank room (82 Elev.) 015A 030-015 Tank room (82 Elev.)

025A 030-025 Tank room (82 Elev.) 106A 030-106 Drum dryer room 026A 030-026 Tank room (82 Elev.) 107A 030-107 Drum dryer room 027A 030-027 Tank room (82 Elev.) 105A 030-105 LRWS equipment room 028A 030-028 Pump room (71 Elev) 033A 030-033 HIC filling room 019A 030-019 Tank room (82 Elev.) 034A 030-034 Class A/B/C HIC Storage 1: Refer to Figure 1.2-28, Figure 1.2-29 and Figure 1.2-30 for room locations.

2 12.3-45 Revision 4

cale Final Safety Analysis Report Area Monitor Estimated Dynamic Principal Parameter Basis for Dynamic Range PAM Variable Detection Range measured Type der bioshield monitors Fixed area 1E+0 to 1E+7 rem/hr gamma RG 1.97, Rev. 3 Type B Equipment Qualification Post-Accident Type C Radiological Source Term Hot lab Fixed area 1E-4 to 1E+4 rem/hr gamma RG 1.97, Rev. 3 Type E ANSI/ANS-HPSSC-6.8.1-1981 Hot lab Fixed airborne 3E-10 to 1E-6 Ci /cc Cs-137: RG 1.97, Rev. 3 Type E Radiological Source Term iation monitors in route Fixed area 1E-4 to 1E+4 rem/hr gamma RG 1.97, Rev. 3 Type E to hot lab ANSI/ANS-HPSSC-6.8.1-1981 fety instrument rooms Fixed area 1E-4 to 1E+4 rem/hr gamma RG 1.97, Rev. 3 Type E ANSI/ANS-HPSSC-6.8.1-1981 SS switchgear rooms Fixed area 1E-4 to 1E+4 rem/hr gamma RG 1.97, Rev. 3 Type E ANSI/ANS-HPSSC-6.8.1-1981 iation monitors in route Fixed area 1E-4 to 1E+4 rem/hr gamma RG 1.97, Rev. 3 Type E safety instrumentation ANSI/ANS-HPSSC-6.8.1-1981 ms and EDSS switchgear rooms RXB access tunnel Fixed area 1E-4 to 1E+4 rem/hr gamma RG 1.97, Rev. 3 Type E ANSI/ANS-HPSSC-6.8.1-1981 MCR envelope - main Fixed area 1E-4 to 1E+4 rem/hr gamma RG 1.97, Rev. 3 Type E trol room area radiation ANSI/ANS-HPSSC-6.8.1-1981 monitor MCR envelope - main Fixed airborne 1E-7 to 1E-1 Ci/cc Kr-85, Xe-133: RG 1.97, Rev. 3 Type E Radiation Protection Design Features control room area 1E-10 to 1E-6 Ci/cc Cs-137: , ANSI/HPS 13.1-2011 orne radiation monitor 1E-10 to 1E-5 Ci/cc I-131:

chnical support center Fixed area 1E-4 to 1E+4 rem/hr gamma RG 1.97, Rev. 3 Type E ANSI/ANS-HPSSC-6.8.1-1981 Primary Sampling Fixed Area 1E-4 to 1E+4 rem/hr gamma RG 1.97, Rev. 3 Type E Equipment ANSI/ANS-HPSSC-6.8.1-1981

cale Final Safety Analysis Report Area Monitor Estimated Dynamic Principal Parameter Basis for Dynamic Range PAM Variable Detection Range measured Type ontainment Sampling Fixed Area 1E-4 to 1E+4 rem/hr gamma RG 1.97, Rev. 3 Type E System Equipment ANSI/ANS-HPSSC-6.8.1-1981 Reactor Building Fixed airborne 3E-7 to 1E+4 Ci/cc Kr-85, Xe-133: Regulatory Guide 1.97, Rev. 3 Type E ontinuous Airborne 5E-12 to 1E+2 Ci/cc Cs-137: , Radiological Source Term Monitor 4E-12 to 1E+2 Ci/cc I-131: ANSI 42.18-2004 Radiation Protection Design Features

cale 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 Ci / cc No elevation 24 Degasifier room B 1 / Noble gas Kr-85, Xe-133: 3E-4 to 1E+3 Ci / cc No eactor Building Hot lab 1 / Particulate Cs-137: 3E-10 to 1E-6 Ci /cc Yes / E elevation 50 eactor Building Reactor Pool 1 / Noble gas Kr-85, Xe-133: 3E-7 to 1E+4 Ci / cc Yes / E evation 100'-0" North Steam Gallery 1 / Particulate Cs-137: , 5E-12 to 1E+2 Ci / cc South Steam Gallery 1 / Iodine I-131: 4E-12 to 1E+2 Ci / cc nnex Building Hot shop 1 / Particulate Cs-137: 3E-10 to 1E-6 Ci /cc No elevation 100 Decontamination shop 1 / Particulate Cs-137: 3E-10 to 1E-6 Ci /cc No dioactive Waste Gaseous radioactive waste 1 / Noble gas Kr-85, Xe-133: 3E-7 to 1E-2 Ci /cc No ding elevation 71 process tank area 1 / Particulate Cs-137: 3E-10 to 1E-6 Ci /cc 1 / Iodine I-131: 3E-10 to 5E-8 Ci /cc ontrol Building Main Control Room 1/Noble Gas Kr-85, Xe-133: 1E-7 to 1E-1 Ci/cc Yes / E levation 76'-6" 1/Particulate Cs-137: , 1E-10 to 1E-6 Ci/cc 1/Iodine I-131: 1E-10 to 1E-5 Ci/cc Radiation Protection Design Features

cale Final Safety Analysis Report Building and Area Detector Quantity / Type Principal Parameter Nominal Range PAM / Type Elevation Measured eactor Building NW stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No elevation 24 NW vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No NW passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No West passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No Pool cleanup filter rooms 2 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No Pool cleanup demineralizers 3 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SW stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SW vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SW passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No NE passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SE passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No NE stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No NE vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No East passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SE stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SE vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No CVCS ion exchanger proximity (serve 12 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No the CVCS reactor coolant filters) eactor Building CVCS pump rooms 12 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No Radiation Protection Design Features levation 35-8

cale Final Safety Analysis Report Building and Area Detector Quantity / Type Principal Parameter Nominal Range PAM / Type Elevation Measured eactor Building NW stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No elevation 50 NW vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No West passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SW stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SW vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SW passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No NW passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No NE passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E CVCS heat exchanger rooms 12 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No NE stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E NE vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E East passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E Hot lab 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E SE stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E SE vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E SE passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E eactor Building NW vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No elevation 62 West passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SW vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No gamma Radiation Protection Design Features SE vestibule 1 / gamma-sensitive 1E-4 to 1E+4 rem/hr No East passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No NE vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No Module heatup system heat exchanger 2 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No rooms

cale Final Safety Analysis Report Building and Area Detector Quantity / Type Principal Parameter Nominal Range PAM / Type Elevation Measured eactor Building NW stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E elevation 75 NW vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E West passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SW stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E SW vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E Safety I&C and EDSS equipment rooms 4 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E SE stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E SE vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E East passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E NE stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E NE vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E eactor Building NW stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E elevation 86 NW vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E Safety I&C and EDSS equipment rooms 4 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E NE stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E NE vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E SE stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E SE vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E SW stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E gamma Radiation Protection Design Features SW vestibule 1 / gamma-sensitive 1E-4 to 1E+4 rem/hr Yes / E

cale Final Safety Analysis Report Building and Area Detector Quantity / Type Principal Parameter Nominal Range PAM / Type Elevation Measured eactor Building NW stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E elevation 100 NW refuel area floor 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No Spent fuel mast bridge (used during 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No fuel movement)

SW stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E SW vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No NE stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E NE vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SE stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E eactor Building SE vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No elevation 100 East passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E NE passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E SE passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E SW refuel area floor 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No Inside bioshield monitor 24 / gamma-sensitive gamma 1E0 to 1E+7 rem/hr Yes / B & C Radiation Protection Design Features

cale Final Safety Analysis Report Building and Area Detector Quantity / Type Principal Parameter Nominal Range PAM / Type Elevation Measured eactor Building NW stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No elevation 126 NW vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SW stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SW vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No NE stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No NE vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SE stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SE vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No NW passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No NE passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SW passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SE passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No Spent fuel pool area 2 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No Reactor pool monitor 10 / gamma-sensitive gamma 1E0 to 1E+7 rem/hr No ontrol Building North entrance space 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No elevation 50 South entrance space 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No South bottle storage room 1 / gamma-sensitive gamma ? 1E-4 to 1E+4 rem/hr No Entrance bottle storage room 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No North bottle storage room 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No Central stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No Radiation Protection Design Features North stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No South stairwell 1 / gamma-sensitive gamma ? 1E-4 to 1E+4 rem/hr No ontrol Building Reactor Building access tunnel 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E levation 76'-6" South stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No Main control room envelope 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E

cale Final Safety Analysis Report Building and Area Detector Quantity / Type Principal Parameter Nominal Range PAM / Type Elevation Measured ontrol Building Technical support center 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E elevation 100 Technical support center hallway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr Yes / E North stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No South stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No ontrol Building Central area 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No elevation 120 North stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No South stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No nnex Building Entry and exit vestibule 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No elevation 100 Hot workshop 1 / gamma-sensitive gamma 1E-5 to 1E+4 rem/hr No Exit turnstiles 1 / gamma-sensitive gamma 1E-5 to 1E+4 rem/hr No Connector to Reactor Building and 1 / gamma-sensitive gamma 1E-5 to 1E+4 rem/hr No Radioactive Waste Building dioactive Waste NE stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No ding elevation 71 SW stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SW passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SE passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No Telecom room area 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No LRWS storage tank pump rooms 4 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No SRWS storage tank pump rooms. 2 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No GRWS heat exchanger room 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No Radiation Protection Design Features GRWS vessel tank room 2 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No Waste drum storage room 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No dioactive Waste LRWS storage tank rooms 8 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No ding elevation 82 SRWS storage tank rooms 4 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No

cale Final Safety Analysis Report Building and Area Detector Quantity / Type Principal Parameter Nominal Range PAM / Type Elevation Measured dioactive Waste Truck bay 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No ilding elevation SW stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No 100 NE stairwell 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No Waste management control room 1 / gamma-sensitive gamma 1E-5 to 1E+4 rem/hr No NE passageway 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No East rollup door area 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No LRWS skids area 1 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No HIC tank rooms storage area 3 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No urbine Building General area 2 / gamma-sensitive gamma 1E-4 to 1E+4 rem/hr No elevation 100 Radiation Protection Design Features

stem System Name System System Name ode Code auxiliary boiler system PSCS pool surge control 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 S condensate and feedwater system RCS reactor coolant system condensate polishing system RPCS reactor pool cooling system S normal control room HVAC system RWBVS Radioactive Waste Building HVAC system S chemical and volume control system RWB Radioactive Waste Building circulating water system RWDS radioactive waste drain system S decay heat removal system RXB Reactor Building SCWS site cooling water system S gaseous radioactive waste system SFPCS spent fuel pool cooling system S liquid radioactive waste system SRWS solid radioactive waste system main steam system UHS ultimate heat sink S pool cleanup system UWS utility water system S pool leakage detection system DWS demineralized water system 2 12.3-56 Revision 4

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The auxiliary boiler system (ABS) uses proven, corrosion resistant material for the system components in accordance with industry codes ntial for leaks or spills and and standards. This design feature also applies to Objective 3.

ide containment areas 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.

ctive 2: Provide leak The ABS is provided with several pressure and level instruments throughout the system to monitor system performance.

ction capability The ABS has four radiation monitors: One on the vent of the high pressure condensate collection tank to monitor the exhaust from the collection tank and prevent the release of radioactive effluents into the atmosphere. The second and third are on the returns from each of the two module heatup system (MHS) heaters to monitor the condensate exiting the MHS heaters to prevent the high pressure boiler system from becoming contaminated in the event of a tube leak in the MHS heaters. The fourth radiation monitor is on the cross-over from the high pressure boiler system to the low pressure boiler system to prevent the low pressure system from becoming contaminated in the event the high pressure system becomes contaminated.

ctive 3: Reduce Isolation valves between the clean and contaminated systems minimize potential for cross-contamination.

amination to minimize Drains are provided for the ABS system and direct the drainage to the balance-of-plant drain system (BPDS) or to the LRWS if it becomes ses, cross-contamination contaminated.

waste generation ctive 4: Facilitate Parts of the ABS (boiler skids and chemical addition skid) are designed using modular vendor skids, which facilitates decommissioning.

mmissioning ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The BPDS uses proven materials in accordance with American Society of Mechanical Engineers (ASME) B31.1. This design feature reduces ntial for leaks or spills and the potential for leaks.

ide containment areas The BPDS uses double-walled pipes with leak detection in the underground piping from the underground sump tanks to the LRWS. This also applies to Objective 2.

The underground BPDS sump tanks are located in stainless steel lined concrete sump pits to provide two boundaries to contain the contents from leaking out of the tank into the concrete or the environment.

The BPDS is a normally non-radioactive system that serves areas that are outside of the RCA. However, design features are included to contain contaminated fluid, if leaks develop from contaminated systems, including sump tanks and sump pumps to prevent overflow conditions.

ctive 2: Provide leak The BPDS interfaces with drains from systems that can become contaminated (i.e. condensate polishing system, ABS, north and south ction capability Turbine Generator Building floor drains). Process radiation monitors are provided in the drain lines from these sources to monitor for radioactive contamination. The sump tanks are provided with level instruments to assist in detecting leaks that are drained to the BPDS.

The underground BPDS sump tanks are equipped with the moisture detectors between the sump tanks and the stainless steel lined concrete sumps to monitor for leaks from the sump tanks.

ctive 3: Reduce The BPDS components are designed for service for the life of the plant. The wetted parts of the piping, valves, tanks, instrumentation, and amination to minimize controls are made of either carbon steel or stainless steel material, depending on the type of chemicals or fluid being processed.

ses, cross-contamination The BPDS drain lines are sloped to facilitate gravity draining and minimize the accumulation of solids.

waste generation The BPDS contents are kept separate from RWDS to minimize waste generation. Liquids from BPDS are sent to LRWS if the radioactive contamination levels warrant.

ctive 4: Facilitate The major, large components of the BPDS are located outside of buildings, allowing easy access to facilitate decommissioning.

mmissioning ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item Radiation Protection Design Features ronmental monitoring

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The containment evacuation system (CES) uses welded components and welded piping to minimize potential for leaks and spills.

ntial for leaks or spills and The use of stainless steel condenser tubes, piping and valve material prevent corrosion leading to pressure boundary failure. This also ide containment areas applies to Objective 3.

The CES equipment vents and drains are directed to LRWS and RWDS. The leaks and spills are routed to the RWDS floor drain hubs via RXB sloped floors.

ctive 2: Provide leak The fixed radiation monitors in proximity of the CES equipment rooms detect high radiation levels in the RXB areas.

ction capability The CES control system uses input from pressure, temperature, flow, and radiation instruments to monitor system performance. The pressure transmitters on the CES condenser and CES sample vessel provide indication that the system may have developed a leak.

The RWDS sumps located in the RXB are equipped with the level transmitter to detect leakage from CES components.

ctive 3: Reduce The CES sample vessel has provisions for flushing with demineralized water and nitrogen.

amination to minimize The clean utility systems that interface with the CES have a minimum of two barriers to prevent cross contamination.

ses, cross-contamination waste generation ctive 4: Facilitate The CES components are designed for the life of the plant and are designed, to the extent practicable, as discreet assemblies to facilitate mmissioning decommissioning. The majority of the CES components are located outside of rooms and cubicles that contain radiation sources. This design feature minimizes equipment contamination and reduces the effort for decommissioning.

ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The CFD containment drain separator tanks are located in a curbed area of the RXB to contain leaks or spills. The drains collected in the ntial for leaks or spills and curbed area are transferred to the RWDS. This also applies to Objective 3.

ide containment areas The CFDS uses corrosion resistant materials that reduce the potential for leaks and contamination.

Major CFDS components are located inside a curbed area to collect and drain leaks to the RWDS. This also applies to Objective 3.

CFDS floors are sloped to collect leaks and direct it to the drain sump within the curbed area.

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

The RWDS sumps located in the RXB are equipped with the level transmitters to detect the piping and valve, pump or tank leakages. This feature warns operators of equipment leakage or spills.

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

ses, cross-contamination waste generation ctive 4: Facilitate The CFDS piping is above the ground and embedded piping is minimized. This design prevents ground contamination and reduces mmissioning decontamination effort during the decommissioning.

ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The condensate and feedwater system (CFWS) piping and components are designed to appropriate industry codes and standards, and are ntial for leaks/ spills and made of corrosion resistant material that is compatible with the operating environment of CFWS. This design feature reduces the potential ide containment areas for leaks.

The welded construction of the CFWS piping, valves, and components reduces the probability of leaks and the spread of contamination.

This also applies to Objective 3.

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

The BPDS monitors the Turbine-Generator Building floor drains for radioactive contamination.

ctive 3: Reduce The CFWS components are selected for reliable service for the life of the plant.

amination to minimize The BPDS handles the drainage from the CFWS, including the chemical wastes drainage or spills. The BPDS system has the capability to ses, cross-contamination & detect radiation and redirect contaminated drainage to the LRWS.

e generation ctive 4: Facilitate The CFWS piping is routed above the ground, as much as possible. This facilitates the decommissioning effort.

mmissioning The CFWS components are mostly located outside the RCA, making it easier to decontaminate and decommission.

ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The condensate polishing system (CPS) demineralizers, regeneration tanks & chemical tanks, pumps, piping, and valves are designed with ntial for leaks or spills and corrosion resistant materials in accordance to the applicable ASME and American Petroleum Institute codes. The welded construction for ide containment areas these components reduces equipment failure and leaks.

The water chemistry exiting the polishers will be maintained to reduce corrosion in the condensate and feedwater systems, steam generators and the steam turbine.

The CPS relief valves on the demineralizers protect the system from over pressurization and prevent damage to the components. The discharge lines from these relief valves are routed to the BPD system.

ctive 2: Provide leak The CPS demineralizer skid, filters and rinse recycle pump skid are provided with a dedicated CPS sump that drains to BPDS drains and to ction capability the BPDS sump. The BPDS sump has level detection to detect leakage.

ctive 3: Reduce The floor and equipment drains are provided for the CPS equipment to direct spills and leaks to the nearest BPDS sump, by gravity, to amination to minimize minimize spread of contamination.

ses, cross-contamination The sluice lines are sized to ensure sufficient velocity is available to prevent resin from settling in the piping system. The resin transfer lines waste generation can be flushed with the feedwater system to minimize personnel exposure when these lines become contaminated.

The resins in the cation and anion regeneration vessels are washed with acid and caustic and recycled back to the CPS. This minimizes waste resin generation.

Utility connections such as service air and demineralized water to CPS are designed with a minimum of two barriers to prevent cross contamination of non-radioactive systems.

The demineralizers and filters/strainers remove radioactivity resulting from primary to secondary leakage to minimize the potential spread of contamination.

ctive 4: Facilitate The CPS components are designed for the life of the plant and are designed, to the extent practicable, as discreet assemblies to facilitate mmissioning decommissioning.

The piping systems are above the ground and embedded piping is minimized, to the extent practical.

ctive 5: Operating programs COL item documentation Radiation Protection Design Features ctive 6: Site radiological COL item ronmental monitoring

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The CRVS air handling units, and fan coil units, located in the CRB provide filtered and conditioned air to maintain the control rooms ntial for leaks or spills and environment within an acceptable range. If the outside air becomes radioactively contaminated, the outside air is filtered. This minimizes ide containment areas the potential for contaminated air from entering the system. This also applies to Objective 3.

The CRVS components are designed, fabricated and tested in accordance with industry codes and standards and constructed using corrosion resistant materials.

The condensation from CRVS components are hard piped to the BPDS. This also applies to Objective 3.

ctive 2: Provide leak The process radiation monitors are provided downstream of the CRVS filter unit. The radiation monitors provide the radiological ction capability contamination levels in the air after being processed by CRVS HEPA filter/charcoal unit.

Duct and housings leak testing is performed after installation in accordance with ASME AG-1, Section TA and Article SA-4500.

Periodic in-place testing of the atmospheric cleanup portions are tested in accordance with RG 1.140 and ASME N510.

The BPD sumps located in the CRB are equipped with level transmitters to detect for leakage.

ctive 3: Reduce The CRVS maintains the areas within the CRB at a positive pressure with respect to the outside environment to minimize the infiltration of amination to minimize air.

ses, cross-contamination The CRVS detects and limits the introduction of airborne radioactivity utilizing radiation monitors and filtration, or isolation dampers, in the waste generation intake duct.

ctive 4: Facilitate The piping and ductwork associated with the CRV system is above ground. This design feature facilitates decommissioning.

mmissioning ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The CVCS tanks, piping, and valves are designed to the applicable ASME code with corrosion resistance materials to minimize degradation ntial for leaks or spills and over the life of the plant. Welded construction is used as practicable, which minimizes the potential for leaks. The CVCS components are ide containment areas located in a Seismic Category I building (RXB).

A chemical mixing tank is provided to allow 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 RWD system.

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 recirculation pumps are canned motor pumps, which minimizes the potential for leaks.

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 for each module are placed in cubicles on elevation 24 of the RXB. These cubicles are ction capability equipped with moisture sensors for early leak detection. The CVCS and MHS heat exchangers and pumps, located on higher elevations, drain to the RWDS sump on elevation 24.

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

The CVCS system provides the capability to inject argon into the RCS which increases the sensitivity to detect SG tube leaks using argon-41.

The CVCS is provided with 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 LRWS, and the NPM injection and discharge lines. The mass flow mismatch indication provides leak detection capability to warn operators of abnormal conditions.

The area radiation monitors near the components can assist in detecting potential leaks.

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

ses, cross-contamination Utility connections are designed with a minimum of two barriers to prevent cross contamination of non-radioactive systems from waste generation potentially radioactive systems.

An automatic diverting three-way valve diverts flow around the ion exchangers if the fluid temperature exceeds the high temperature Radiation Protection Design Features setpoint for Ion Exchanger resin protection, preventing resin damage, and minimizing waste generation.

The equipment drains and vents from the CVCS are sent to the RWDS and eventually transferred to the LRWS, and can be recycled back into the CVCS or RCS to minimize waste generation.

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

Drain and vent lines for CVCS and MHS major equipment (pumps, tanks, heat exchangers, filters, and resin traps) allow for the direct draining into the equipment drain system prior to maintenance activities. This reduces the potential spread of contamination.

cale Final Safety Analysis Report Objective Design Features ctive 4: Facilitate The CVCS components are designed for the life of the plant and are designed, to the extent practicable, as discreet assemblies to facilitate mmissioning decommissioning.

The CVCS components are designed with flushing capabilities. Design features, such as welding techniques and surface finishes, are included to facilitate decontamination processes.

Embedded CVCS piping is minimized, as much as practical.

ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The circulating water system (CWS) is designed to minimize the effects of corrosion using a combination of corrosion resistant materials, ntial for leaks/ spills and cathodic protection and water treatment with corrosion inhibitors. This also applies to Objective 3.

ide containment areas The CWS provides cooling water to the tube side of the turbine-generators main condensers and operates at a higher pressure than the condenser shell side to keep leakage out of CWS and into the condenser. This also applies to Objective 3.

ctive 2: Provide leak Grab samples are periodically taken from the cooling tower basin to monitor the water chemistry and for radioactive contamination.

ction capability CWS leakage into the Turbine Generator Building will be collected by the BPDS, which is monitored for radionuclide contamination.

ctive 3: Reduce The CWS components are designed for service for the life of the plant.

amination to minimize ses, cross-contamination &

e generation ctive 4: Facilitate The CWS is a normally non-contaminated system that is protected by multiple barriers from contaminated systems (SG tubes, condenser mmissioning tubes, and higher operating pressure than the condensing steam) and is periodically monitored for contamination, reducing the probability and magnitude of contamination that will facilitate eventual decommissioning.

ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring Radiation Protection Design Features

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

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

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

waste generation ctive 4: Facilitate The DHRS is designed for the full service life of the plant and is designed, to the extent practicable, for easy removal.

mmissioning ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The GRWS uses low-leakage valves, such as packless metal diaphragm valves, wherever possible to minimize the potential for leaks.

ntial for leaks or spills and Proven materials and welded construction are used to minimize leaks.

ide containment areas Embedded piping is minimized and liquid containing lines are sloped to facilitate drainage. This also applies to Objective 4.

Adequate charcoal is provided in each train of the GRWS to reduce the gaseous radioactive effluents to minimize amount of contaminated gas released to the RBVS and or the environment. This also applies to Objective 3.

ctive 2: Provide leak Gas analyzers will detect potentially explosive gas mixtures to enable operators to prevent an event that would challenge system boundary ction capability integrity.

Leak detection is provided by area airborne radiation monitors.

ctive 3: Reduce The GRWS component materials are selected for reliable service for the life of the plant, reducing waste generation from replacing these amination to minimize components.

ses, cross-contamination Components are designed with materials that are compatible with the operating environment, as well as meeting codes and standards waste generation identified in RG 1.143.

Connections with clean utility systems are designed with at least two barriers to prevent cross-contamination of the clean systems.

The process piping containing contaminated fluid is sloped to facilitate flow and reduce traps, thus reducing waste generation.

Welding techniques and material finishes are designed to provide smooth internal surfaces for easy decontamination. This also applies to Objective 4.

The GRWS piping arrangements use manifolds, as much as practical, to reduce the amount of piping.

The GRWS process radiation monitors return the sampled stream back to the process stream. This feature reduces waste generation.

In-line radiation monitors minimize the spread of contamination and waste generation by returning sampled gas back to the process stream.

ctive 4: Facilitate The GRWS components are designed, to the extent practical, as individual elements, for ease of removal during decommissioning.

mmissioning Nitrogen is provided to purge and decontaminate the system internals prior to disassembly and decommissioning.

ctive 5: Operating programs COL item Radiation Protection Design Features documentation ctive 6: Site radiological COL item ronmental monitoring

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The LRWS uses proven materials and welded construction in accordance with applicable codes and standards for piping, valves and ntial for leaks or spills and components. This design minimizes leaks and contamination of the facility and the environment. This feature is also applicable to ide containment areas Objective 3.

The LRWS tanks are designed to provide adequate holdup capacity of the liquid waste generated in the plant. The HCW and LCW collection and sample tanks are cross-tied to provide operational flexibility and the space needed for storing waste during abnormal conditions. This feature prevents tank overflow and spread of contamination.

The LRWS is provided with two processing skids that are similar in design and can process either waste type (HCW or LCW). This design feature minimizes the tank overflows, and spread of contamination.

The tank overflow lines are sized for maximum surge input. The discharge lines are routed close to the floor to prevent tank surface, adjacent walls or the personnel becoming contaminated.

The LRWS piping located in RWB is above ground to the extent practicable, except for the double-walled buried pipe located in the discharge pipe from the sample collection tanks. The double-walled pipe annulus is pressurized to prevent leakage to the environment.

The tank level instruments in the LRWS facilitate automated pump starting and stopping. This design approach minimizes tank overflow and prevents the spread of contamination.

The LRWS collection, and sample tanks are located in a separate shielded concrete cubicle with stainless steel liner to contain the entire volume of each tank.

ctive 2: Provide leak Pressure transmitters on the pressurized tanks such as degasifier, ion exchangers, and charcoal bed (granulated activated charcoal) provide ction capability system pressure boundary failure information.

The LRWS tank cubicles are provided with drains that are directed to the RWDS sump tanks, which have level instruments to detect leaks.

The LRWS tanks are equipped with the level detectors to monitor tank level changes, leaks or overflow conditions.

Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 3: Reduce The LRWS components are selected for reliable service for the life of the plant, reducing waste generation. The wetted parts of piping, amination to minimize valves, tanks, filter housing, instrumentation, and controls are made of corrosion resistant material.

ses, cross-contamination The LRWS has the capability to recycle processed water back into the plant systems. This feature minimizes the waste generation.

waste generation The LRWS has CIP skids for cleaning or flushing collection tanks, sample tanks, equipment processing skids and sluicing resin out of the LRWS demineralizer vessels. The CIP prevents cross contamination of the demineralized water system (DWS).

The LRWS tanks are either vented directly into HVAC ductworks, or vented into a canopy type vent to prevent contaminating the air space.

The level transmitter instruments on the collection, sample, and detergent tanks have diaphragm seal design to prevent instruments from becoming contaminated. This feature reduces the quantities of contaminated equipment requiring decontamination or disposal during the decommissioning period.

The LRWS collection tanks, sample tanks, and detergent tanks have conical bottom design to reduce crud or solid buildup at the bottom.

Pipe connections with the clean utility systems are designed with at least two barriers to prevent cross-contamination of the clean system.

The relief valves are provided on the degasifier vessels and the demineralizers to prevent tank over pressurizations. The relief valve discharge lines are routed close to the floor to reduce the spread of contamination.

The process piping that contains contaminated fluid is sloped to facilitate flow and reduce fluid traps, thus reducing contamination.

Welding techniques and material finishes are designed to minimize leaks and provide for easy decontamination. This design feature also applies to Objective 4.

The LRWS tanks are strategically located to collect wastes from various sources. These wastes are segregated for different handling and processing requirements to minimize cross-contamination.

The LRWS is designed with redundant equipment. The pumps are sized for maximum input to prevent overflow; one pump is normally used during normal operation. If one pump is out of service, the backup pump can be used to prevent overflow condition and the spread of contamination.

The demineralizer skid has 5 vessels with different media. Each vessel has a bypass line to bypass it if not needed for processing the water.

This feature minimizes resin usage (waste generation).

ctive 4: Facilitate The LRWS components are designed for full service life. The LRWS processing equipment is skid mounted which facilitates easy removal for mmissioning decommissioning.

The LRWS is designed with minimum embedded or buried piping. The contaminated lines are routed through pipe chases as much as Radiation Protection Design Features practicable. This design approach facilitates decommissioning.

The collection and sample tanks are enclosed in shielded concrete cubicles with a stainless steel liner. The liner extends to a level sufficient to contain the volume of liquid in the tank. This reduces contamination of the concrete and facilitates decommissioning.

CIP flush water or the DWS break tank is provided to flush and decontaminate the equipment in the LRWS prior to maintenance or preparation for decommissioning.

ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The main steam system (MSS) piping is made of corrosion resistant materials and designed in accordance with ASME code. The fluid ntial for leaks or spills and chemistry is maintained to reduce corrosion and minimize the potential for system leaks. This also applies to Objective 3.

ide containment areas MSS uses welded connections for piping and equipment, except where threaded or flanged joints are required for maintenance. This 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 area radiation monitors can assist in detecting steam leaks into the RXB.

The condenser air removal system radiation monitors are designed to monitor effluents coming from the condenser air removal system and are designed to detect SG tube leaks.

ctive 3: Reduce Fluid leaks from the MSS in the RXB and TGB are collected by the RWDS and BPDS, respectively.

amination to minimize The CPS is provided to cleanup the secondary coolant to reduce the level of radionuclide contamination and minimize releases, cross-ses, cross-contamination contamination, and waste generation.

waste generation A minimum of two barriers is provided between clean systems (non-radioactive systems), such as the nitrogen distribution system and the ABS, and the MSS to prevent cross-contamination.

ctive 4: Facilitate The MSS components are designed for the life of the plant and are designed, to the extent practicable, as discreet assemblies to facilitate mmissioning decommissioning. The piping and equipment are above ground, as much as practicable..

The MSS piping have smooth surfaces and are sloped to reduce decontamination efforts and facilitate decommissioning.

ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The PCUS uses proven materials for piping and components including valves, filter housings, and demineralizers.

ntial for leaks or spills and The PCUS is designed with minimum embedded or buried piping. The contaminated lines are routed through the pipe chases as much as ide containment areas practicable. This feature also applies to Objective 4.

The PCUS components are located in a separate shielded cubicle inside the RXB to ensure leakage wont spread to adjacent areas. The sloped floors in each cubicle direct leakage to the nearest RWDS drain hub.

The PCUS components (demineralizers, filters, and resin traps) have vents and drains that are hard piped to the RWDS.

ctive 2: Provide leak An area radiation monitor is provided in each equipment room to assist in detecting spills and leaks.

ction capability The PCUS is provided with multiple instruments (pressure, level, flow, pressure differential across filters and demineralizers) to monitor system performance and detect pressure boundary failure.

ctive 3: Reduce Components are designed with materials that are compatible with the operating environment. The wetted parts of piping, valves, amination to minimize demineralizers, filter housing, instrumentation, and controls are made of stainless steel material to reduce corrosion to reduce the potential ses, cross-contamination & for equipment failures.

e generation The filters and demineralizers remove impurities and minimize pool contamination. The PCUS has the capability to recycle the pool water after being filtered and demineralized. This feature reduces waste generation.

Temperature transmitters upstream of the PCUS demineralizers protect the resin from being exposed to high temperature, preventing the damage of resins and reducing waste generation.

Connections with the DWS are designed with at least two barriers to prevent cross-contamination of clean system.

Relief valves are provided on the demineralizer vessels to prevent over pressurizations. The relief valves discharge lines are routed close to the floor to reduce the spread of contamination.

The PCUS demineralizers and resin traps are provided with flushing capability to reduce the contamination levels within the system. This also applies to Objective 4.

ctive 4: Facilitate The PCUS components are designed for full service life and easily removable elements during decommissioning.

mmissioning The PCUS is designed with minimum embedded or buried piping. The contaminated lines are routed through pipe chases as much as practicable.

Radiation Protection Design Features Demineralized water break tank water is provided to flush and decontaminate equipment in the PCUS prior to maintenance or preparation for decommissioning.

ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The pool leakage detection system (PLDS) has leak channels behind the pool wall liner and under the pool floor liner to guide pool leaks to ntial for leaks or spills and a drain header that leads to RWDS sumps. The PLDS uses welded channels and piping to minimize potential for leaks. Pool leaks are ide containment areas designed to flow through the leak channels to the RWDS sumps.

The PLDS uses stainless steel material to prevent corrosion. This feature reduces the potential for leaks. This also applies to Objective 3.

ctive 2: Provide leak The RWDS sumps, located in the RXB, are equipped with level transmitters to detect leakage from the pool liner.

ction capability ctive 3: Reduce The PLDS is designed with corrosion resistant materials for the wetted parts (leak channels, piping, and valves). The selected material is amination to minimize compatible with the operating environment of the pool water.

ses, cross-contamination The PLDS drain lines from the leak channels are gravity drained to the RWDS through enclosed pipes. This design feature prevents spread of waste generation contamination.

ctive 4: Facilitate The PLDS is designed for full service life of the plant. With the exception of the leak channels embedded into the concrete, the individual mmissioning drain lines and the main header are above the ground. This design feature facilitates decommissioning.

ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Table 12.3-29: Regulatory Guide 4.21 Design Features for Pool Surge Control System Objective Design Features ctive 1: Minimize the The PSCS is designed with a catch basin to contain the total volume of the PSCS storage tank plus freeboard. The catch basin contains the ntial for leaks or spills and leakage and transfers the fluid to the LRWS collection tanks. Using stainless steel components and piping reduces corrosion and the ide containment areas potential for leaks.

The welded stainless steel collection tank and piping system reduces the potential for leaks.

The pool water from a surge event is processed through the PCUS and stored in the pool 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 also applies to Objective 3.

The floor of the catch basin collects leakage and directs it to the drain sump within the catch basin. The sump transfers this fluid to the LRWS, minimizing the spread of contamination. This also applies to Objective 3.

The use of underground, or buried piping, is minimized to the extent practicable. The PSCS is designed with double-walled pipe for lines between the RXB, RWB, and the yard (PSCS storage tank), reducing the potential for contamination of the environment. This also applies to Objective 4.

ctive 2: Provide leak The sump located in the catch basin is equipped with a level transmitter to detect tank leakage.

ction capability The PSCS storage tank located within the catch basin is equipped with the level transmitter to detect the tank leakage.

ctive 3: Reduce The PSCS storage tank bottom and the catch basin floor are sloped to reduce the potential for contamination buildup. The catch basin drain amination to minimize sump sends the water to the LRWS. Any leakage from the double-walled pipe annulus is directed to the RWDS. This feature minimizes the ses, cross-contamination potential for environmental contamination.

waste generation ctive 4: Facilitate The PSCS components are designed for the life of the plant and are designed, to the extent practicable, as discreet assemblies to facilitate mmissioning decommissioning.

ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The PSS uses proven materials to minimize leaks and contamination of the facility and the environment. Welded construction is used as ntial for leaks or spills and appropriate to minimize the potential for leakage from contaminated systems.

ide containment areas 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. This includes 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 sample. 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 sample panels are located in the RXB.

ction capability 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 operating environment. The wetted parts of piping, valves, amination to minimize pump, heat exchangers, analyzers, grab sample containers, instrumentations, and controls are made of stainless steel material to reduce ses, cross-contamination & corrosion.

e generation The automatic samples are returned back to the originating system as much as practical 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 sample 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 at least two barriers to prevent cross-contamination.

The PSS welding techniques and material finishes are designed to minimize leaks and provide smooth internal surfaces for easy Radiation Protection Design Features decontamination.

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 full service life with easily removable elements during decommissioning.

mmissioning The PSS is designed with minimal embedded or buried piping. The contaminated lines are routed through the pipe chases as much as practicable.

ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring

cale Final Safety Analysis Report System ctive Design Features ctive 1: Minimize the Periodic in-place testing of the atmospheric portions of RBVS is performed in accordance with RG 1.140 and ASME N510.

ntial for leaks or spills and The RBVS components are designed, fabricated and tested according to industry codes and standards, and constructed using corrosion ide containment areas resistant materials.

The condensations drains from RBVS components are directed to RWDS drain sumps. This also applies to Objective 3.

ctive 2: Provide leak The RWDS sumps located in the RXB are equipped with 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 outside environment to prevent potentially contaminated air amination to minimize from leaking to the environment.

ses, cross-contamination The air handling units and fan coil units are provided with filters to reduce the potential contamination levels of the air.

waste generation 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 minimize contamination of equipment and facilitates mmissioning decommissioning.

The RBVS piping and ductwork is above ground. This design feature facilitates decommissioning.

ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The reactor component cooling water system (RCCWS) is normally a clean closed loop (non-radioactive) system, and consists of piping and ntial for leaks/ spills and equipment that are made of stainless steel that is compatible with the RCCWS operating environment. This minimizes corrosion and ide containment areas potential leaks. This also applies to Objective 3.

The RCCWS is located in the RXB with sloped floors that direct drainage to the nearest drain hub. This also applies to Objective 3.

ctive 2: Provide leak The RCCWS is provided with process radiation monitors downstream of interfacing heat exchangers to detect cross contamination due to ction capability heat exchanger leakage.

The RWDS RCCW 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 life of the plant.

amination to minimize The RCCWS is a closed loop intermediate system that removes heat from radioactive systems and transfers that heat to SCWS that releases ses, cross-contamination & the heat to the environment. The use of RCCWS as an intermediate cooling loop reduces the potential for releasing contamination.

e generation The RCCWS interface with the DWS is designed with a minimum of two barriers to prevent cross-contamination of the DWS.

ctive 4: Facilitate The RCCWS piping and equipment are made of stainless steel material with smooth surfaces to facilitate decontamination and mmissioning decommissioning. The DWS can be used for cleaning and flushing purposes to remove contamination.

ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The reactor coolant system (RCS) is entirely contained within the reactor pressure vessel (RPV), which is an ASME BPVC Section III, Class 1 ntial for leaks or spills and vessel, and is periodically inspected according to the applicable portions of ASME Section XI (See Section 5.2.4).

ide containment areas Penetrations on the upper vessel head are welded such that potential leakage from these penetrations will be confined within the containment vessel.

The RCS components are designed for the life of the plant using nuclear industry-proven materials compatible with the operating environment. This also applies to Objective 4.

ctive 2: Provide leak RCS leaks into the SG will be detected by radiation monitors associated with the MSS or the condenser air removal system. Leakage ction capability monitoring for the SGs is in accordance with EPRI 97-06 (See 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 (see Section 5.2.5).

The CVCS system 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, reducing the contamination levels in the RCS.

amination to minimize Materials used in the RCS are low in nickel and cobalt content, to the maximum extent practical, to reduce contamination due to crud.

ses, cross-contamination The CVCS provides the capability to inject zinc into the RCS to help reduce corrosion product generation and deposition.

waste generation ctive 4: Facilitate Sharp geometric discontinuities and recesses have been avoided to the extent practical in the RCS design in order to minimize flow mmissioning dependent pressure loss and to minimize regions where activated corrosion products can accumulate. The RCS piping and equipment have smooth surfaces. This design feature facilitates decommissioning.

The RCS is designed as part of a module that will facilitate decommissioning.

ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL Item ronmental monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The six-inch curb around the reactor pool cooling system (RPCS) heat exchangers in the RXB is designed to contain the leaks or spills. This ntial for leaks or spills and also applies to Objective 3.

ide containment areas The RPCS piping is designed according to ASME B31.1 using corrosion resistant materials, like stainless steel, for piping, valves, pumps, and wetted parts of the heat exchangers.

ctive 2: Provide leak The RPCS has temperature, pressure, conductivity, and flow instruments to monitor system performance and to assist in identifying system ction capability leaks.

The RWD sumps located in the RXB are equipped with level transmitters to detect RPCS leaks.

Although the SCWS is normally at a higher pressure than RPCS, radiation detectors are provided in the site cooling water system to detect RPCS heat exchanger tube leaks into the SCWS.

ctive 3: Reduce The RPCS interfaces with the PCUS for the cleanup of the pool water to reduce the contamination levels.

amination to minimize The RPCS equipment vents, drains, and relief valve discharges are hard piped to a drain hub to minimize the spread of contamination.

ses, cross-contamination Isolation arrangements are provided for major components to allow flushing using the vent and drain connections.

waste generation ctive 4: Facilitate The RPCS components are designed for the life of the plant and are designed, to the extent practicable, as discreet assemblies to facilitate mmissioning decommissioning.

An epoxy coating is applied for the areas surrounding the suction strainers, pumps and heat exchangers to minimize contamination of concrete and facilitate decommissioning. This also applies to Objective 3.

The RPCS components are above ground and embedded piping is minimized. This design prevents ground contamination and facilitates decommissioning.

ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Conditioning System Objective Design Features ctive 1: Minimize the Periodic in-place testing of the atmospheric portions of RWBVS is performed in accordance with RG 1.140 and ASME N510.

ntial for leaks or spills and The RWBVS components are designed, fabricated and tested according to industry codes and standards, and constructed using corrosion ide containment areas resistant materials.

The condensation drains from RWBVS components are directed to RWDS drain sumps. This 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 are equipped with level transmitters to detect leakage.

ctive 3: Reduce The RWBVS maintains the RWB atmosphere at a negative pressure relative to the outside environment to prevent potentially contaminated amination to minimize air from leaking to the environment.

ses, cross-contamination The air handling units and fan coil units are provided with filters to reduce the potential contamination levels of the air.

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 minimize contamination of equipment and facilitate mmissioning decommissioning.

The RWBVS piping and ductwork are above ground. This design feature facilitates decommissioning.

ctive 5: Operating programs COL item documentation ctive 6: Site Radiological COL item ronmental Monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The RWBS is designed with the shielded tank cubicles to contain the total volume of each tank. Each tank room in the RWB that contains ntial for leaks or spills and radioactive fluid has a welded stainless steel liner. Wall penetrations below the liquid containment level are minimized.

ide containment areas The RWB floors are sloped to collect floor surface drainage and direct it to the appropriate RWDS drain hub to minimize the spread of contamination.

Embedded floor drains in the RWB are minimized to extent practicable.

The RWB is designed with a minimum number of structural joints to contain water and provide protection against ground water intrusion.

The penetrations below grade are minimized as much as practicable.

ctive 2: Provide leak See Objective 6.

ction capability ctive 3: Reduce The equipment rooms that contain radioactive fluids are designed with curbs or walls to prevent leaks from spreading into the other areas.

amination to minimize The RWB is designed with pipe chase and a concrete tunnel between the RWB and RXB to provide a shielded pathway for contaminated ses, cross-contamination lines, to minimize the spread of contamination. The concrete tunnel will collect leaks to RWDS, is inspectable, and prevents ground water waste generation intrusion.

The RWB is designed to minimize use of structural joints and wall penetrations below the liquid containment level to prevent leaks in one area from cross-contaminating adjacent areas.

ctive 4: Facilitate Surfaces with the potential for contamination are protected with an epoxy coating to minimize contamination of concrete and facilitate mmissioning decommissioning.

ctive 5: Operating programs COL item documentation ctive 6: Site Radiological COL item ronmental Monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The RWDS uses proven materials and welded construction for the system components, including the sump liners.

ntial for leaks or spills and Each sump has two pumps and a level instrument to facilitate automated pump starting and stopping. This design approach reduces the ide containment areas potential of sump overflow and the spread of contamination.

ctive 2: Provide leak The CVCS demineralizer cubicles are equipped with a moisture detector for early leak detection.

ction capability The RWDS sump tanks have leak detection capability (moisture sensor) 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 life of the plant, reducing waste generation from replacing components.

amination to minimize Loop seals have been provided at various elevations of the RXB and RWB to prevent air cross-contamination between the floors and the ses, cross-contamination rooms with a common drain header.

waste generation The chemical drain tank has a conical bottom design to reduce crud buildup.

Pipe connections with the clean utility system are designed with at least two barriers to prevent cross-contamination.

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.

Welding techniques and material finishes are designed to provide smooth internal surfaces to facilitate decontamination. This also applies to Objective 4.

The RWDS sump tanks are strategically located to collect floor and equipment drains from various sources. The drains are segregated (floor, equipment, chemical, RCCW, and detergent drains) for different handling and processing requirements to minimize cross-contamination.

Sump tanks vent directly into the HVAC system (ductwork) to reduce airborne contamination.

The floor drains on upper elevation of the RXB and the RWB contain loop seals to prevent spread of airborne contamination between the building elevations or the rooms that are connected to the same drain header.

ctive 4: Facilitate The RWDS is designed with minimum embedded piping, as much as practicable. Drain lines are routed through pipe chases as much as mmissioning practicable. Piping between buildings (RXB, RWB, and ANB) is routed through the pipe chases provided between the buildings.

The instruments downstream of the sump pumps have diaphragm seal design to prevent instruments from becoming contaminated. This feature reduces the quantities of contaminated equipment requiring disposal during the decommissioning period.

Radiation Protection Design Features ctive 5: Operating programs COL item documentation ctive 6: Site Radiological COL item ronmental Monitoring

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The RXBS equipment rooms are designed with curbs and shielded cubicles. This feature minimizes the spread of contamination.

ntial for leaks or spills and The welded stainless steel liner for the pool and dry dock minimize the potential of leakage.

ide containment areas RXB floors are sloped to facilitate the collection of floor surface drainage and direct it to the nearest RWDS drain hub.

The RXB is designed with a minimum number of structural joints to prevent contamination of the environment and provide protection against ground water intrusion. The RXB basemat is placed monolithically.

ctive 2: Provide leak See Objective 6.

ction capability ctive 3: Reduce The equipment rooms that contain radioactive fluids are designed with curbs or walls to prevent leaks from spreading into other areas.

amination to minimize The RXB is designed with a concrete tunnel between the RXB and RWB to provide a pathway for contaminated lines, to minimize the spread ses, cross-contamination contamination. The concrete tunnel collects leaks to RWDS, is inspectable, and prevents ground water intrusion.

waste generation There are no subgrade penetrations through the RXB exterior walls.

ctive 4: Facilitate Surfaces with the potential for contamination are protected with an epoxy coating to minimize contamination of concrete and facilitate mmissioning decommissioning.

ctive 5: Operating programs COL item documentation ctive 6: Site Radiological COL item ronmental Monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The SCWS is normally a clean (non-radioactive) system that supplies cooling water to heat loads in the Reactor Building, Central Utility ntial for leaks/ spills and Building, North and South Turbine Generator Buildings, and the Auxiliary Boiler Building. The SCWS piping that is underground is reinforced ide containment areas or pre-stressed concrete pressure pipe designed to American Water Works Association standards. The SCWS piping that is above ground is made of carbon steel designed to ASME B31.1. These designs are compatible with the operating environment of the SCWS. This minimizes corrosion and reduces the potential for leaks. This also applies to Objective 3.

The SCWS is equipped with a chemical feed system to add biocides, despersants, corrosion and scale inhibitors to minimize system degradation and potential leakage.

ctive 2: Provide leak The SCW system is provided with process radiation monitors downstream of heat exchangers for the RCCWS, spent fuel pool cooling system ction capability (SFPCS), and RPCS, and on the cooling tower overflow and blowdown lines to the utility water system (UWS) discharge basin. These radiation monitors are provided to detect cross contamination due to leaks from heat exchangers.

Grab sampling capability is also provided to measure radiation contamination levels in the system.

ctive 3: Reduce The SCWS components are selected for reliable service for the life of the plant.

amination to minimize ses, cross-contamination &

e generation ctive 4: Facilitate The SCWS is provided with both process radiation monitors and sampling provisions to monitor for water quality and contamination and mmissioning alert operators to take corrective measures. This approach will minimize the contamination levels of the SCWS and facilitate decommissioning. This also applies to Objective 3.

ctive 5: Operating programs COL item documentation ctive 6: Site Radiological COL item ronmental Monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The six-inch curb around the SFPCS pumps, strainers, and heat exchangers in the RXB is designed to contain leaks and spills. This also ntial for leaks or spills and applies to Objective 3.

ide containment areas The SFPCS piping is designed according to ASME B31.1 and uses stainless steel piping, valves, pumps, and wetted parts of the heat exchangers to resist corrosion and reduce the potential for leaks.

The RXB floors are sloped and coated with epoxy to collect surface drainage and direct it to the RWDS drain sump. This also applies to Objective 3.

ctive 2: Provide leak The area radiation monitor in proximity of the SFPCS heat exchanger area detects high radiation conditions, warning operators of abnormal ction capability condition. This feature minimizes personnel exposure.

Although the site cooling water system is normally at a higher pressure than SFPCS, radiation detectors are provided in the SCWS to detect RPCS heat exchanger tube leaks into the SCWS.

The RWDS sumps located in the RXB are equipped with the level transmitters to detect SFPCS leaks.

ctive 3: Reduce The concrete floors will have special coating (epoxy) to prevent spills penetrating the concrete and creating permanent fixed amination to minimize contamination.

ses, cross-contamination The SFPCS is designed with a minimum of two barriers between the SFPCS and the clean systems to prevent cross-contamination.

waste generation The SFPCS equipment vents and drains are connected to the equipment drain hub to minimize contamination of floors.

The SFPCS interfaces with the PCUS for the cleanup of the pool water to reduce contamination levels.

ctive 4: Facilitate The SFPCS components are designed for the life of the plant and are designed, to the extent practicable, as discreet assemblies to facilitate mmissioning decommissioning.

The SFPCS components are above ground and embedded pipe is minimized. This design prevents ground contamination and facilitates decommissioning.

ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The SRWS tanks, piping, and valves are designed with a corrosion resistance material in accordance with code and standards from RG 1.143 ntial for leaks or spills and to minimize degradation over the life of the plant.

ide containment areas The welded construction of components and piping minimize of the potential for failures and leaks as compared with flanged joints.

Relief valves on each tank protect the tanks from over pressurization. The RV discharge lines are routed close to the floor to prevent contaminating the tank exterior surfaces, cubicle walls and personnel who work in the area.

The SRWS equipment (tanks and pumps) are placed in a separate cubicles to limit the spread of contamination from leaks. Each SRWS storage tank cubicle has stainless steel lined walls to contain the contents of the tank.

The spent cartridge filter transport cask is equipped with a drip pan to capture drips from the spent filter during transport.

ctive 2: Provide leak The resin storage tanks are equipped with two level transmitters to detect level changes in the tanks associated with the tank leakages.

ction capability The dewatering fill head is equipped with a level transmitter, level control valve, and a CCTV camera on the fill head for monitoring high integrity container (HIC) level during the filling process.

The area radiation monitors near the SRWS components can assist in detecting potential leaks and spills.

The waste storage areas and the radioactive waste building crane are designed with remote cameras, which provide monitoring capability.

RWDS sumps are equipped with level transmitters to detect liquid accumulation.

ctive 3: Reduce The slurry lines are sized to ensure sufficient velocity to prevent resins from settling in the piping system during resin transfer. The piping is amination to minimize designed with five-diameter bend elbows to reduce fluid or slurry traps, thus reducing contamination and waste generation.

ses, cross-contamination The SRWS resin storage tanks are designed with conical bottoms to reduce the collection of resins or sludge.

waste generation Connections from normally clean utility systems are designed with a minimum of two barriers to prevent cross-contamination from potentially radioactive systems.

The HEPA filter downstream of the dewatering fillhead and the compactor capture radioactive particles prior to being discharged to the RWBVS.

The internal resin screens on the vent line, pump suction, and break pot tank prevent contaminated resin from entering the RWBVS or pump suction.

Resin sluice operations using resin storage tank decant water minimizes waste generation as compared to feed and bleed method using Radiation Protection Design Features clean water.

Three pump suction connections on the side of each resin storage tank minimize use of demineralized water needed for sluicing operations.

The slurry lines are provided with full port ball valves to reduce crud buildup and resin traps.

The level or pressure transmitters are designed with diaphragm type instrument lines.

The top sluicing tank design reduces line blockage or hot spots in the resin transfer lines during resin transfers to a HIC. The line drains back into the storage tank by gravity when the transfer is terminated.

cale Final Safety Analysis Report Objective Design Features ctive 4: Facilitate The SRWS equipment is designed for the life of the plant and designed, to the extent practicable, as discreet assemblies to facilitate mmissioning decommissioning.

The SSC are designed with decontamination capabilities using the CIP skids. Design features, such as welding techniques and surface finishes are included to facilitate decontamination and minimize waste generation.

The instruments that interface with contaminated fluid or slurry are designed with diaphragm seals to reduce decontamination requirements during decommissioning.

The SRWS is designed with above ground piping, to the extent practical.

ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The UHS pool liner plates and the piping system are designed and fabricated according to industry codes and standards. This minimizes the ntial for leaks or spills and potential for leaks. This applies to objective 3 for cross contamination.

ide containment areas The UHS uses stainless steel piping, valve, and pool liner material to reduce the potential that corrosion will result in leaks. This feature also applies to Objective 3.

The UHS components are welded to minimize of the potential for leakage and spreading contamination to the plant or environment. 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 The UHS components are designed for the life of the facility using nuclear industry-proven materials compatible with the operating amination to minimize environment.

ses, cross-contamination The water inventory within the UHS is provided with cleanup capability through the PCUS filters and demineralizers to reduce the waste generation contamination level of the water.

ctive 4: Facilitate The UHS components are designed to facilitate decommissioning with welded, stainless steel surfaces for easier decontamination.

mmissioning ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The UWS above ground piping is constructed of coated carbon steel or equivalent materials compatible with the operating conditions and ntial for leaks/ spills and designed in accordance with ASME B31.1. The UWS underground piping is reinforced, pre-stressed, or both, concrete pressure pipe, as ide containment areas applicable, designed to the American Water Works Association standards. Using proven material in accordance with applicable codes and standards minimizes the potential for leaks.

ctive 2: Provide leak The UWS discharge basin outfall is the monitored single point liquid effluent release path to the environment and includes a radiation ction capability monitor, plus sampling provisions.

ctive 3: Reduce The UWS components are selected for reliable service for the life of the plant.

amination to minimize ses, cross-contamination &

e generation ctive 4: Facilitate The portion of the UWS that may become contaminated is the discharge basin, limiting the amount of equipment needed to be mmissioning decontaminated during decommissioning.

ctive 5: Operating programs COL item documentation ctive 6: Site radiological COL item ronmental monitoring Radiation Protection Design Features

cale Final Safety Analysis Report Objective Design Features ctive 1: Minimize the The DWS tanks and piping system are designed and fabricated according to industry codes and standards. This minimizes the potential for ntial for leaks or spills and leaks. This feature also applies to Objective 3.

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

The DWS tanks are welded to minimize of the potential for leakage and spreading contamination to the plant or environment. This feature also applies to Objective 3.

ctive 2: Provide leak Samples are routinely taken from the DWS to test for contaminants that may have leaked into the DWS.

ction capability The DWS incorporates radiation monitors to detect the backflow of contamination into the DWS.

ctive 3: Reduce The DWS includes backflow preventers at the connections to systems throughout the plant to minimize the probability of contaminating amination to minimize the DWS distribution system. The DWS supply headers are segregated based on supplying either clean or contaminated systems.

ses, cross-contamination, waste generation ctive 4: Facilitate The DWS components are designed for full service life with elements that can be easily removed during decommissioning.

mmissioning ctive 5: Operating programs COL Item documentation ctive 6: Site radiological COL Item ronmental monitoring Radiation Protection Design Features

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-1a: Reactor Building Radiation Zone Map - 24' Elevation

(( Withheld - See Part 9 Tier 2 12.3-91 Revision 4

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-1b: Reactor Building Radiation Zone Map - 35'-8" Elevation (( Withheld - See Part 9 }} Tier 2 12.3-92 Revision 4

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-1c: Reactor Building Radiation Zone Map - 50' Elevation (( Withheld - See Part 9 }} Tier 2 12.3-93 Revision 4

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-1d: Reactor Building Radiation Zone Map - 62' Elevation (( Withheld - See Part 9 }} Tier 2 12.3-94 Revision 4

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-1e: Reactor Building Radiation Zone Map - 75' Elevation (( Withheld - See Part 9 }} Tier 2 12.3-95 Revision 4

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-1f: Reactor Building Radiation Zone Map - 86' Elevation (( Withheld - See Part 9 }} Tier 2 12.3-96 Revision 4

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-1g: Reactor Building Radiation Zone Map - 100' Elevation (( Withheld - See Part 9 }} Tier 2 12.3-97 Revision 4

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-1h: Reactor Building Radiation Zone Map - 126' Elevation (( Withheld - See Part 9 }} Tier 2 12.3-98 Revision 4

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-1i: Reactor Building Radiation Zone Map - 146' Elevation (( Withheld - See Part 9 }} Tier 2 12.3-99 Revision 4

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-2a: Radioactive Waste Building Radiation Zone Map - 71' Elevation (( Withheld - See Part 9 }} Tier 2 12.3-100 Revision 4

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-2b: Radioactive Waste Building Radiation Zone Map - 100' Elevation (( Withheld - See Part 9 }} Tier 2 12.3-101 Revision 4

Bioshield RXP Concrete Division Walls CNV Shell Pressurizer Region RPV Shell Homogenized Steam Generator Region Homogenized Upper Riser Region Homogenized Lower Riser Region Reflector Core 2 12.3-102 Revision 4

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-4a: Not Used Tier 2 12.3-103 Revision 4

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-4b: Not Used Tier 2 12.3-104 Revision 4

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-4c: Not Used Tier 2 12.3-105 Revision 4

NuScale Final Safety Analysis Report Radiation Protection Design Features Figure 12.3-4d: Not Used Tier 2 12.3-106 Revision 4

The dose assessment presented in this section includes the estimated radiation exposures to plant personnel performing work activities involving normal operations, maintenance and inspections, refueling activities, and waste handling, using the methodology presented in Regulatory Guide (RG) 8.19 to demonstrate that the facility design is compliant with 10 CFR 20. The dose assessment process is integrated into the overall ALARA program during the design of the NuScale Power Plant facility to help maintain occupational radiation exposures as low as reasonably achievable. To estimate the occupational radiation exposures for the NuScale facility, various work activities and work durations are compiled along with the expected significant (>0.1 mrem/hr) radiation fields that would be encountered. 4.1 Occupational Radiation Exposure Radiation exposures to plant operating personnel are determined in accordance with the methods described in RG 8.19. The radiation protection features described in Section 12.3, together with the health physics program discussed in Section 12.5, maintain operator occupational radiation exposure as low as reasonably achievable. The airborne concentrations in various parts of the facility are provided in Section 12.2. The calculated occupational exposure estimates were developed to reflect the expected dose rates in a facility at any point during its operation. In the absence of operational dose information, the sources in Section 12.2 were used to inform some of the assumed dose rates used for occupational exposures. The estimated annual occupational radiation exposures are calculated from the following activity categories:

• reactor operations and surveillances
• routine maintenance
• inservice inspection
• special maintenance
• waste processing
• refueling activities The total estimated annual occupational personnel doses are summarized in Table 12.4-1.

Details for each work activity assessed are discussed below. 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. 4.1.1 Reactor Operations and Surveillance During plant operations, systems and components are monitored for performance and operating condition. This monitoring includes operator rounds during each shift. Some examples of the specific activities performed by operators include: 2 12.4-1 Revision 4

• 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 the calculated values of the collective doses for reactor operations and surveillances.

4.1.2 Routine Inspection and Maintenance Routine inspection and maintenance activities are performed for plant components during plant operations. These routine 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 lists work activities and their respective doses for routine inspection and maintenance. 4.1.3 Inservice Inspection Periodic inservice inspections are required to be performed on 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. Detailed listings of the doses associated with major inservice inspection activities are provided in Table 12.4-4. 4.1.4 Special Maintenance Special maintenance consists of activities that go beyond routine scheduled maintenance. This includes 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. Special maintenance activities for each NPM are assumed to occur once every two years, based on a two-year refueling cycle. Special maintenance activities consist of the following:

• control rod drive mechanism electromagnetic coil replacement
• in-core instrumentation maintenance 2 12.4-2 Revision 4
• valve maintenance or replacement
• valve position indicator calibration
• steam generator tube cleaning and plugging
• pressurizer heater replacement Table 12.4-5 provides the estimated doses due to special maintenance operations. The estimated dose is for up to a 12-NPM site with six refueling outages per year.

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 operation, waste maintenance, and other activities. Waste operation 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. Estimated annual doses from waste processing operations are listed in Table 12.4-6. 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 major activities included in the dose assessment for refueling activities include:

• 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 2 12.4-3 Revision 4

various refueling activities. 4.1.7 Overall Plant Doses The estimated annual personnel doses associated with the activities discussed above are summarized in Table 12.4-1. Occupational personnel dose estimates are calculated assuming a 12-NPM site and 24-month fuel cycle for NPM operation, which equates to six refueling outages per year. 4.1.8 Post-Accident Actions There are no vital areas, as defined by NUREG-0737, Item II.B.2, other than the areas for initiating combustible gas monitoring (described in Section 9.3.2.2.3), the main control room, and the technical support center, which are in compliance with 10 CFR 50.34(f)(2)(vii). There are no credited post-accident operator actions outside of the main control room for design basis events, as described in Chapter 15. The operator dose assessments for the main control room and the technical support center are provided in Section 15.0.3. 4.1.9 Construction Activities For the construction of an additional NuScale Power Plant adjacent to an existing NuScale Power Plant, the estimated annual radiation exposure to a construction worker is estimated based upon a construction staffing plan over the estimated construction period. It is estimated that the annual dose for a construction worker is 1.64 mrem/year. Item 12.4-1: A COL applicant that references the NuScale Power Plant design certification 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. 2 12.4-4 Revision 4

Activity Category Percent of Total Estimated Annual Dose (man-rem) tor operations & surveillance 8% 2.6 ine maintenance & inspections 7% 2.2 vice inspection 15% 5.0 ial maintenance 30% 10 te processing 4% 1.4 eling 35% 11.5 l 100% 33

Estimates assume a plant with 12 NPMs on a two year refueling cycle.

2 12.4-5 Revision 4

Activity Category Average Dose Rate Exposure Time Estimated Annual Dose (mrem/hr) (man-hr/year) (man-rem) rity patrols 0.08 380 0.03 rations 0.31 4300 1.3 th Physics surveys 0.19 3300 0.64 mistry 0.03 2400 0.08 eillance 0.19 1900 0.36 identification 2.0 78 0.16 ations 0.06 160 0.01 l 0.21 12,000 2.6

Estimates assume a plant with 12 NPMs on a two year refueling cycle.

2 12.4-6 Revision 4

Activity Average Dose Rate Exposure Time Estimated Annual Dose (mrem/hr) (man-hr/year) (man-rem) levation 1.6 50 0.08 Elevation 1.6 380 0.61 levation 0.96 780 0.75 levation 1.8 35 0.06 levation 0.09 5 0.0004 Elevation 0.18 2300 0.42 machine shop 2 160 0.32 l 0.61 3700 2.2

Estimates assume a plant with 12 NPMs on a two year refueling cycle.

2 12.4-7 Revision 4

Activity Average Dose Rate Exposure Time Estimated Annual Dose (mrem/hr) (man-hr/year) (man-rem) preparation work 0.69 3170 2.19 m generator 8.7 147 1.28 ainment vessel side 5.0 8.22 0.04 tor pressure vessel side 32 26.0 0.83 ainment vessel head 5.0 15.9 0.08 tor pressure vessel head 20 33.5 0.67 l 1.48 3400 5.0

Estimates assume a plant with 12 NPMs on a two year refueling cycle.

2 12.4-8 Revision 4

Inspection Location Average Dose Rate Annual Time Estimated Annual Dose (mrem/hr) (man-hrs) (man-rem) rol rod drive mechanism 12 385 4.6 re instrumentation 20 108 2.2 umentation 8 192 1.5 es 9 72 0.65 e position indicators 7.4 69 0.51 m generators 7.7 59 0.46 surizer heaters 14 12 0.17 ls 11 897 10

Estimates assume a plant with 12 NPMs on a two year refueling cycle.

2 12.4-9 Revision 4

Activity Average Dose Rate Exposure Time Estimated Annual Dose (mrem/hr) (man-hr/year) (man-rem) e Operation 0.39 1300 0.51 e Maintenance 0.54 370 0.20 r Waste Activities 0.30 2200 0.66 l 0.35 3900 1.4

Estimates assume a plant with 12 NPMs on a two year refueling cycle.

2 12.4-10 Revision 4

NPM Refueling Activity Activity Time Estimated Annual (man-hrs) Dose (man-rem) are NPM for movement 105 0.28 onnect and move NPM to containment vessel flange tool 46 0.10 ssemble NPM 178 0.03 plete lower containment vessel work 20 0.13 el reactor 133.0 0.27 semble and move module to operating bay 230 0.18 nnect NPM 196 0.83 sition to operations 35 0.10 upational radiation exposure for one NPM refueling outage 943 1.92 ual Refueling occupational radiation exposure (6 NPMs) 5660 11.5

Estimates assume a plant with 12 NPMs on a two year refueling cycle.

2 12.4-11 Revision 4

2 12.4-12 Revision 4 Item 12.5-1: A COL applicant that references the NuScale Power Plant design certification 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. 2 12.5-1 Revision 4}}