Text

Technical Requirements Manual Offsite Dose Calculation Manual Volume II
	ML081220235
Person / Time
Site:	Fermi
Issue date:	01/03/2008
From:	; DTE Energy
To:	; Office of Nuclear Reactor Regulation
References
	FOIA/PA-2010-0209, NRC-08-0031
	Download: ML081220235 (177)
	v • d • e

Frwmi z Technical Requirem ents Manual

~Offsite Dose Calculation Manual Volume 11 Detroit

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OFFSITE DOSE CALCULATION MANUAL Pages Revised in Latest Revision 0-1, 3-10, 3-13, 3-24, 3-26, 3-32, 3-33, 3-35, 3-37, 5-4, 7-2, 7-4, 7-10, 7-13, 7-14, 7-17, 9-3, Il 1107 10-5, 10-6, 10-13, 10-14, and 10-15.

Implementation Plan These revisions go into effect upon approval.

FERMI 2 ODCM - TRM VOLUME II 0-1 rN Mev.

7 /0'7

TABLE OF CONTENTS Page Section 1-1

1.0 INTRODUCTION

PART I - RADIOLOGICAL EFFLUENT CONTROLS 2-1 2.0 DEFINITIONS 3-1 3.0 CONTROLS AND SURVEILLANCE REQUIREMENTS 3-2 314.0 Controls and Surveillance Requirements Applicability 3-5 3/4.3.7.11 Radioactive Liquid Effluent Monitoring Instrumentation 3-10 3/4.3.7.12 Radioactive Gaseous Effluent Monitoring Instrumentation 3-17 3/4.11.1.1 Liquid Effluents Concentration 3-21 3/4.11.1.2 Liquid Effluents Dose 3-22 314.11.1.3 Liquid Waste Treatment 3-23 3/4.11.2.1 Gaseous Effluents Dose Rate 3-27 314.11.2.2 Gaseous Effluents Dose - Noble Gases 3-28 3/4.11.2.3 Gaseous Effluents Dose - Iodine-1 31, Iodine-1 33, Tritium, and Radionuclides in Particulate Form 3-29 3/4.11.2.4 Offgas Treatment System 3-30 3/4.11.2.5 Ventilation Exhaust Treatment System 3-31 3/4.11.2.8 Venting or Purging 3-32 314.11.4 Radioactive Effluents Total Dose 3-33 3/4.12.1 Radiological Environmental Monitoring Program 3-44 3/4.12.2 Land Use Census 3-45 3/4.12.3 Interlaboratory Comparison Program 4-1 4.0 BASES 5-1 5.0 ADMINISTRATIVE CONTROLS 5-2 5.9.1.7 Annual Radiological Environmental Operating Report 5-2 5.9.1.8 Annual Radioactive Effluent Release Report 5-4 5.15 Major Changes to Radioactive Liquid, Gaseous, and Solid Waste Treatment Systems FERMI 2 ODCM - TRM VOLUME II 0-2 Rev. 13

TABLE OF CONTENTS (continued)

Page Section PART II - CALCULATIONAL METHODS 6-1 6.0 LIQUID EFFLUENTS 6-2 6.1 Radiation Monitoring Instrumentation and Controls 6-2 6.1.1 Offsite Dose Calculation Manual (ODCM) 3.3.7.11 Requirement 6-3 6.1.2 Non-ODCM Required Monitor 6-4 6.2 Sampling and Analysis of Liquid Effluents 6-4 6.2.1 BATCH Releases 6-5 6.2.2 CONTINUOUS Releases 6-5 6.3 Liquid Effluent Monitor Setpoints 6-6 6.3.1 Liquid Radwaste Effluent Line Monitor 6-9 6.3.2 Circulating Water Reservoir Decant Line Radiation Monitor (DI1-N402) 6-10 6.3.3 Generic, Conservative Alarm Setpoint for D1I-N402 6-11 6.3.4 Alarm Setpoint for GSW and RHR System Radiation Monitors 6-11 6.3.5 Alarm Response - Evaluating Actual Release Conditions 6-12 6.3.6 Liquid Radwaste Setpoint Determination With Contaminated Circulating Water Reservoir 6-13 6.4 Contaminated GSW or RHR System - Quantifying and Controlling Releases 6-14 6.5 Liquid Effluent Dose Calculation - 10 CFR 50 6-14 6.5.1 MEMBER OF THE PUBLIC Dose - Liquid Effluents 6-16 6.5.2 Contaminated CWR System - Dose Calculation 6-17 6.6 Liquid Effluent Dose Projections 7-1 7.0 GASEOUS EFFLUENTS 7-2 7.1 Radiation Monitoring Instrumentation and Controls 7-2 7.1.1 Effluent Monitoring - Ventilation System Releases 7-2 7.1.2 Main Condenser Offgas Monitoring 7-3 7.1.3 Reactor Building Ventilation Monitors (Gulf Atomic) 7-3 7.2 Sampling and Analysis of Gaseous Effluents 7-3 7.2.1 Containment PURGE 7-4 7.2.2 Ventilation System Releases FERMI 2 ODCM - TRM VOLUME II 0-3 Rev. 13

TABLE OF CONTENTS (continued)

Page Section 7-5 7.3 Gaseous Effluent Monitor Setpoint Determination 7-5 7.3.1 Ventilation System Monitors 7-7 7.3.2 Setpoint Determination with No Nuclides Detected 7-7 7.3.3 Gaseous Effluent Alarm Response - Evaluating Actual Release Conditions 7-8 7.4 Primary Containment VENTING and PURGING 7-8 7.4.1 Release Rate Evaluation 7-9 7.4.2 Alarm Setpoint Evaluation 7-10 7.5 Quantifying Releases - Noble Gases 7-10 7.5.1 Sampling Protocol 7-11 7.6 Calculation of Activity Released 7-11 7.7 Site Boundary Dose Rate - Radioiodine and Particulates 7-13 7.8 Noble Gas Effluent Dose Calculations - 10 CFR 50 7-13 7.8.1 UNRESTRICTED AREA Dose - Noble Gases 7-14 7.9 Radioiodine and Particulate Dose Calculations - 10 CFR 50 7-14 7.9.1 UNRESTRICTED AREA Dose - Radioiodine, Particulates, and Tritium 7-16 7.10 Gaseous Effluent Dose Projection 8-1 8.0 SPECIAL DOSE ANALYSES 8-2 8.1 Doses Due to Activities inside the SITE BOUNDARY 8-2 8.2 Doses to MEMBERS OF THE PUBLIC - 40 CFR 190 8-3 8.2.1 Effluent Dose Calculations 8-4 8.2.2 Direct Exposure Dose Determination 8-4 8.2.3 Dose Assessment Based on Radiological Environmental Monitoring Data 9-1 9.0 ASSESSMENT OF LAND USE CENSUS DATA 9-2 9.1 Land Use Census as Required by ODCM 3.12.2 9-4 9.2 Land Use Census to Support Realistic Dose Assessment FERMI 2 ODCM - TRM VOLUME II 0-4 Rev. 13

TABLE OF CONTENTS (continued)

Paae Section 10-1 10.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 10-2 10.1 Sampling Locations 10-2 10.2 Reporting Levels 10-3 10.3 Interlaboratory Comparison Program TABLES Paae Table 2-7 2.1 Surveillance Frequency Notation 2-8 2.2 Operational Conditions 3-6 3.3.7.11-1 Radioactive Liquid Effluent Monitoring Instrumentation 3-8 4.3.7.11-1 Radioactive Liquid Effluent Monitoring Instrumentation Surveillance Requirements 3-11 3.3.7.12-1 Radioactive Gaseous Effluent Monitoring Instrumentation 3-14 4.3.7.12-1 Radioactive Gaseous Effluent Monitoring Instrumentation Surveillance Requirements 3-18 4.11.1.1.1-1 Radioactive Liquid Waste Sampling and Analysis Program 3-24 4.11.2.1.2-1 Radioactive Gaseous Waste Sampling and analysis Program 3-35 3.12.1-1 Radiological Environmental Monitoring Program 3-40 3.12.1-2 Reporting Levels for Radioactivity Concentrations in Environmental Samples 3-41 4.12.1-1 Detection Capabilities for Environmental Sample Analysis 6-19 6.0-1 Fermi 2 Site Specific Liquid Ingestion Dose Commitment Factors, Aio 6-21 6.0-2 Bioaccumulation Factors (BFi)

FERMI 2 ODCM - TRM VOLUME II 0-5 Rev. 1-3

TABLE OF CONTENTS (continued)

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TABLES (continued)

Pnnn Thble Pane Table 7-17 7.0-1 Values for Evaluating Gaseous Release Rates and Alarm Setpoints 7-18 7.0-2 Dose Factors for Noble Gases 7-19 7.0-3 Controlling Locations, Pathways and Atmospheric Dispersion for Dose Calculations 7-20 7.0-4 Gaseous Effluent Pathway Dose Commitment Factors 8-8 8.0-1 Assumptions for Assessing Doses Due to Activities inside SITE BOUNDARY 8-9 8.0-2 Recommended Exposure Rates in Lieu of Site Specific Data 10-4 10.0-1 Radiological Environmental Monitoring Program, Fermi 2 Sample Locations and Associated Media FIGURES Paae Fioure 3-46 3.0-1 Map Defining Unrestricted Areas and Site Boundary for Radioactive Gaseous and Liquid Effluents 6-22 6.0-1 Liquid Radioactive Effluent Monitoring and Processing Diagram 7-50 7.0-1 Gaseous Radioactive Effluent Monitoring and Ventilation Systems Diagram END OF SECTION 0.0 FERMI 2 ODCM - TRM VOLUME 1R 0-6 Rev. 13

Nuclear Production - Fermi 2 ODCM-2.0 Offsite Dose Calculation Manual Page 2.0-1 PART I RADIOLOGICAL EFFLUENT CONTROLS

r SECTION

1.0 INTRODUCTION

FERMI 2 ODCM - TRM VOLUME II 1-1 Rev. 13

1.0 INTRODUCTION

Part I of the Fermi 2 Offsite Dose Calculation Manual (ODCM), which includes Sections 2.0 through 5.0, contains the controls and surveillance requirements for radioactive effluents and radiological environmental monitoring. It also contains requirements for the Annual Radiological Environmental Operating Report and the Annual Radioactive Effluent Release Report.

This satisfies the requirements for Technical Specification 5.5.1, the Offsite Dose Calculation Manual (ODCM), and Technical Specification 5.5.4, Radioactive Effluent Controls Program.

Part II of the ODCM describes the methodology and parameters used in calculating radioactive liquid and gaseous effluent monitoring instrumentation alarm/trip setpoints, and in calculating liquid and gaseous effluent dose rates and cumulative doses.

The methodology provided in Part II of this manual is acceptable for use in demonstrating compliance with the dose limits for members of the public of 10 CFR 20, the cumulative dose criteria of 10 CFR 50, Appendix I and 40 CFR 190, and the controls in Part I of this manual.

Part II, Section 6.0 of the ODCM describes equipment for monitoring and controlling liquid effluents, sampling requirements, and dose evaluation methods. Section 7.0 provides similar information on gaseous effluent controls, sampling, and dose evaluation. Section 8.0 describes special dose analyses required for compliance with Fermi 2 Offsite Dose Calculation Manual and 40 CFR 190. Section 9.0 describes the role of the annual land use census in identifying the controlling pathways and locations of exposure for assessing potential off-site doses.

Section 10.0 describes the Radiological Environmental Monitoring Program.

The ODCM will be maintained at Fermi 2 for use as a listing of radiological effluent controls and surveillance requirements, as well as a reference guide and training document for accepted methodologies and calculations. Changes to the ODCM calculational methodologies and parameters will be made as necessary to ensure reasonable conservatism in keeping with the principles of 10 CFR 50.36a and Appendix I for demonstrating that radioactive effluents are "As Low As Reasonably Achievable."

NOTE: Throughout this document words appearing all capitalized denote either definitions specified in the Fermi 2 Controls or common acronyms.

END OF SECTION 1.0 FERMI 2 ODCM - TRM VOLUME II 1-2 Rev. 14

SECTION 2.0 DEFINITIONS FERMI 2 ODCM - TRM VOLUME II 2-1 Rev. 13

2.0 DEFINITIONS Term Definition ACTIONS ACTIONS shall be that part of a Specification that prescribes Required Actions to be taken under designated Conditions within specified Completion Times.

CHANNEL CALIBRATION A CHANNEL CALIBRATION shall be the adjustment, as necessary, of the channel output such that it responds within the necessary range and accuracy to known values of the parameter that the channel monitors. A CHANNEL CALIBRATION shall encompass the entire channel including the required sensor, alarm, display, and trip functions, and shall include a CHANNEL FUNCTIONAL TEST. Calibration of instrument channels with resistance temperature detectors (RTD) or thermocouple sensors may consist of an inplace qualitative assessment of sensor behavior and normal calibration of the remaining adjustable devices in the channel. A CHANNEL CALIBRATION may be performed by means of any series of sequential, overlapping, or total channel steps so that the entire channel is calibrated.

CHANNEL CHECK A CHANNEL CHECK shall be the qualitative assessment, by observation, of channel behavior during operation. This determination shall include, where possible, comparison of the channel indication and/or status with other indications and/or status derived from independent instrument channels measuring the same parameter.

CHANNEL FUNCTIONAL TEST A CHANNEL FUNCTIONAL TEST shall be the injection of a simulated or actual signal into the channel as close to the sensor as practicable to verify FUNCTIONAL CAPABILITY, including required alarm, interlock, display, and trip functions, and channel failure trips. A CHANNEL FUNCTIONAL TEST may be performed by means of any series of sequential, overlapping, or total channel steps so that the entire channel is tested.

FERMI 2 ODCM - TRM VOLUME II 2-2 Rev. 14

Term Definition FREQUENCY NOTATION The FREQUENCY NOTATION specified for the performance of Surveillance Requirements shall correspond to the intervals defined in Table 2.1.

FUNCTIONALLY CAPABLE A system, subsystem, division, component, or device shall be FUNCTIONALLY CAPABLE or have FUNCTIONAL CAPABILITY when it is capable of performing its specified safety function(s) and when all necessary attendant instrumentation, controls, normal or emergency electrical power, cooling and seal water, lubrication, and other auxiliary equipment that are required for the system, subsystem, division, component, or device to perform its specified safety function(s) are also capable of performing their related support function(s).

MEMBER(S) OF THE PUBLIC MEMBER(S) OF THE PUBLIC means any individual except when that individual is receiving an occupational dose.

MODE A MODE shall correspond to any one inclusive combination of mode switch position, average reactor coolant temperature, and reactor vessel head closure bolt tensioning specified in Table 2.2 with fuel in the reactor vessel.

MPC (Maximum Permissible Concentration in water) For individual nuclides, 10 times the concentration values in 10 CFR Part 20.1001-20.2402, Appendix B, Table 2, Column 2, except for noble gases which are-limited to 2E-4 uCi/ml total activity concentration. For nuclide mixtures, concentrations for which the sum of individual nuclide concentrations divided by their corresponding individual MPC values equals 1.

OCCUPATIONAL DOSE OCCUPATIONAL DOSE means the dose received by an individual in the course of employment in which the individual's assigned duties involve exposure to radiation and/or to radioactive material from licensed and unlicensed sources of radiation, whether in the possession of the licensee or other person. Occupational dose does not include dose received from background radiation, as a patient from medical practices, from voluntary participation in medical research programs, or as a member of the general public.

FERMI 2 ODCM - TRM VOLUME II 2-3 Rev. 14

Term Definition OFF-GAS An OFF-GAS TREATMENT SYSTEM is any system TREATMENT SYSTEM designed and installed to reduce radioactive gaseous effluents by collecting reactor coolant system offgases from the reactor coolant and providing for delay or holdup for the purpose of reducing the total radioactivity prior to release to the environment.

OFFSITE DOSE The OFFSITE DOSE CALCULATION MANUAL (ODCM)

CALCULATIONAL MANUAL shall contain the methodology and parameters used in the calculation of offsite doses resulting from radioactive gaseous and liquid effluent, in the calculation of gaseous and liquid effluent monitoring alarm/trip setpoints, and in the conduct of the radiological environmental monitoring program. The ODCM shall also contain (1) the Radiological Effluent Controls and Radiological Environmental Monitoring Program Controls, and (2) descriptions of the information that should be included in the Annual Radiological Environmental Operating and Annual Radioactive Effluent Reports required by Controls 5,9.1.7 and 5.9.1.8.

PUBLIC DOSE PUBLIC DOSE means the dose received by a member of the public from exposure to radiation and/or radioactive material released by a licensee, or to any other source of radiation under the control of a licensee. It does not include occupational dose or doses received from background radiation, as a patient from medical practices, or from voluntary participation in medical research programs.

PURGE - PURGING PURGE or PURGING is the controlled process of discharging air or gas from a confinement to maintain temperature, pressure, humidity, concentration or other operating condition, in such a manner that replacement air or gas is required to purify the confinement.

RATED THERMAL POWER RTP shall be a total reactor core heat transfer rate to the (RTP) reactor coolant of 3430 MWt.

REPORTABLE EVENT A REPORTABLE EVENT shall be any of those conditions specified in Section 50.73 to 10 CFR Part 50.

I FERMI 2 ODCM - TRM VOLUME II 2-4 Rev. 14

Term Definition SITE BOUNDARY The SITE BOUNDARY shall be that line beyond which the land is neither owned, nor leased, nor otherwise controlled, by the licensee.

SOURCE CHECK A SOURCE CHECK shall be the qualitative assessment of channel response when the channel sensor is exposed to a radioactive source.

THERMAL POWER THERMAL POWER shall be the total reactor core heat transfer rate to the reactor coolant.

UNRESTRICTED AREA The Fermi 2 Energy Center UNRESTRICTED AREA includes all areas outside the site boundary.

VENTILATION EXHAUST A VENTILATION EXHAUST TREATMENT SYSTEM shall TREATMENT SYSTEM be any system designed and installed to reduce gaseous radioiodine or radioactive material in particulate form in effluents by passing ventilation or vent exhaust gases through charcoal adsorbers'and/or HEPA filters for the purpose of removing iodines or particulates from the gaseous exhaust stream prior to the release to the environment. Such a system is not considered to have any effect on noble gas effluents. Engineered Safety Feature (ESF) atmospheric cleanup systems are not considered to be VENTILATION EXHAUST TREATMENT SYSTEM components.

VENTING VENTING shall be the controlled process of discharging air or gas from a confinement to maintain temperature, pressure, humidity, concentration or other operating condition, in such a manner that replacement air or gas is not provided or required during VENTING. Vent, used in system names, does not imply a VENTING process.

FERMI 2 ODCM - TRM VOLUME II 2-5 Rev. 14

TABLE 2.1 SURVEILLANCE FREQUENCY NOTATION NOTATION FREQUENCY S...................................................... At least once per 12 hours1.388889e-4 days 0.00333 hours 1.984127e-5 weeks 4.566e-6 months .

D ................................................ At least once per 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months .

W .................................................... At least once per 7 days.

M...................................................... At least once per 31 days.

Q.... .............................................. At least once per 92 days.

SA ..................................................... At least once per 184 days.

A...................................................... At least once per 366 days.

R..ý........................................ .... ....... At least once per 18 months (550 days).

SU .................................. ...... ........ Prior to each reactor startup.

P .................................................... Prior to each radioactive release.

Nk.A .......... . .........

........... . Not applicable.

FERMI 2 ODCM - TRM VOLUME 11 2-6 Rev. 14

TABLE 2.2 MODES REACTOR MODE AVERAGE REACTOR MODE TITLE SWITCH POSITION COOLANT TEMPERATURE (OF) 1 Power Operation Run NA 2 Startup Refuel(") or Startup/Hot NA Standby 3 Hot Shutdown(") Shutdown > 200 4 Cold Shutdown(a) Shutdown < 200 5 Refueling(b) Shutdown or Refuel NA (a) All reactor vessel head closure bolts fully tensioned.

(b) One or more reactor vessel head closure bolts less than fully tensioned.

END OF SECTION 2.0 FERMI 2 ODCM - TRM VOLUME II 2-7 Rev. 14

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SECTION 3.0 CONTROLS AND SURVEILLANCE REQUIREMENTS FERMI 2 ODCM - TRM VOLUME II 3-1 Rev. 13

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3/4 CONTROLS AND SURVEILLANCE REQUIREMENTS 3/4.0 APPLICABILITY CONTROLS 3.0.1 Controls shall be met during the MODES or other specified conditions in the Applicability, except as provided in Control 3.0.2.

3.0.2 Upon discovery of a failure to meet a Control, the Actions shall be met, except as provided in Control 3.0.5.

If the Control is met or is no longer applicable prior to expiration of the specified completion time(s),. completion of the Action(s) is not-required, unless otherwise stated.

3. 0:3 When a Control is not met and the associated ACTIONS are not met, an associated ACTION is not provided, or if directed by the associated ACTIONS, the unit shall be placed in a MODE or other specified condition in which the Control is not applicable. Action shall be initiated within 1 hour1.157407e-5 days 2.777778e-4 hours 1.653439e-6 weeks 3.805e-7 months to place the unit, as applicable, in:

1. Mode 2 within 7 hours8.101852e-5 days 0.00194 hours 1.157407e-5 weeks 2.6635e-6 months ;

2. Mode 3 within 13 hours1.50463e-4 days 0.00361 hours 2.149471e-5 weeks 4.9465e-6 months ; and

3. Mode 4 within 37 hours4.282407e-4 days 0.0103 hours 6.117725e-5 weeks 1.40785e-5 months .

Exceptions to this Control are stated in the individual Controls.

Where corrective measures are completed that permit operation in accordance with the Control 0r ACTIONS, completion of the actions required by Control 3.0.3 is not required.

Control 3.0.3 is only applicable in MODES 1, 2, and 3.

FERMI 2 ODCM - TRM VOLUME 1I32Re.1 3-2 Rev. 14

3/4.0 APPLICABILITY CONTROLS (continued) 3.0.4 When a Control is not met, entry into a MODE or other specified condition in the Applicability shall not be made except when the associated ACTIONS to be entered permit continued operation in the MODE or other specified condition in the*

Applicability for an unlimited period of time. This Specification shall not prevent changes in MODES or other specified conditions in the Applicability that are required to comply with ACTIONS or that are part of a shutdown of the unit.

Exceptions to this Control are stated in the individual Controls. These exceptions allow entry into MODES or other specified conditions in the Applicability when the associated ACTIONS to be entered allow unit operation in the MODE or other specified condition in the Applicability only for a limited period of time.

,Control 3.0.4 is only applicable for entry into a MODE or~other specified condition in the Applicability in MODES 1, 2, and 3.

3.0.5 Equipment removed from service or declared not FUNCTIONALLY CAPABLE to comply with ACTIONS may be returned to service under administrative control solely to perform testing required to demonstrate its FUNCTIONAL CAPABILITY or the FUNCTIONAL CAPABILITY of other equipment. This is an exception to Control 3.0.2 for the system returned to service under administrative control to perform the testing required to demonstrate FUNCTIONAL CAPABILITY.

FERMI 2 ODCM - TRM VOLUME 1133Re.1 3-3 Rev. 14

314.0 APPLICABILITY SURVEILLANCE REQUIREMENTS 4.0.1 Surveillance Requirements shall be met during the MODES or other specified conditions in the Applicability for individual Controls, unless otherwise stated in the Surveillance Requirements. Failure to meet a Surveillance, whether such failure is experienced during the performance of the Surveillance or between performances of the Surveillance, shall be failure to meet the Control. Failure to perform a Surveillance within the specified Frequency shall be failure to meet the Control except as provided in Surveillance Requirement 4.0.3. Surveillances do not have to be performed on equipment which is not FUNCTIONALLY CAPABLE or variables outside specified limits.

4.0.2 .The specified Frequency is met if the Surveillance is performed within 1.25 times the interval specified in the Frequency, as measured from the previous pIerformance or as measured from the time a specified condition of the Frequency is met.

For Frequencies specified as "once," the above interval extension does not apply.

If a Completion Time requires periodic performance on a "once per .. "basis, the above Frequency extension applies to each performance after the initial performance.

Exceptions to this Control are stated in the individual Controls.

4.0.3 If it is discovered that a Surveillance was not performed within its specified Frequency, then compliance with the requirement to declare the Control not met may be delayed, from the time of discovery, up to 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months or up to the limit of the specified Frequency, whichever is greater. This delay period is permitted to allow performance of the Surveillance. A risk evaluation shall be performed for any Surveillance delayed greater than 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months and the risk impact shall be managed.

I,f the Surveillance is not performed with'in the delay period, the Control must immediately be declared not met, and the applicable ACTIONS must be entered.

When the Surveillance is performed within the delay period and the Surveillance is not met, the Control must immediately be declared not met, and the applicable ACTIONS must be entered.

4 0.4 Entry into a MODE or other specified condition in the Applicability of a Control shall not be made unless the Control's Surveillances have been met within their specified Frequency. This provision shall not prevent entry into MODES or other specified conditions in the Applicability that are required to comply with ACTIONS or that are part of a shutdown of the unit.

4.0.4 is only applicable for entry into a MODE or other specified condition in the Applicability in MODES 1.t 2, and 3.

FERMI 2 QDCM - TRM VOLUME 1134Re.1 3-4 Rev. 15

INSTRUMENTATION

(*

RADIOACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION CONTROLS 3.3.7.11 The radioactive liquid effluent monitoring instrumentation channels shown in Table 3.3.7.11-1 shall be FUNCTIONALLY CAPABLE with their alarm/trip setpoints set to ensure that the limits of Control 3.11.1.1 are not exceeded. The alarm/trip setpoints of these channels shall be determined and adjusted in accordance with the methodology and parameters in the OFFSITE DOSE CALCULATIONAL MANUAL (ODCM).

APPLICABILITY: At all times.

ACTION:

a. With a radioactive liquid effluent monitoring instrumentation channel alarm/trip setpoint less conservative than required by the above control, immediately suspend the release of radioactive liquid effluents monitored by the affected channel, or declare the channel not FUNCTIONALLY CAPABLE, or change the setpoint so it is acceptably conservative.

b. With less than the minimum number of radioactive liquid effluent monitoring instrumentation channels FUNCTIONALLY CAPABLE, take the ACTION shown in Table 3.3.7.11-1. Restore the instrumentation which is not FUNCTIONALLY CAPABLE to FUNCTIONALLY CAPABLE status within 30 days and, if unsuccessful, explain why this condition was not corrected in a timely manner in the next Annual Radioactive Effluent Release Report.

c. The provisions of Controls 3.0.3 and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS 4.3.7.11 Each radioactive liquid effluent monitoring instrumentation channel shall be demonstrated FUNCTIONALLY CAPABLE by performance of the CHANNEL CHECK, CHANNEL CALIBRATION, and CHANNEL FUNCTIONAL TEST operations at the frequencies shown in Table 4.3.7.11-1.

FERMI 2 ODCM - TRM VOLUME II 3-5 Rev. 13

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TABLE 3.3.7.11-1 RADIOACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION lnstrumentý.inlmum.Chann.i Action

1. GROSS RADIOACTIVITY MONITORS PROVIDING ALARM AND AUTOMATIC TERMINATION OF RELEASE

a. Liquid Radwaste Effluent Line D11-N007 1 110

2. GROSS RADIOACTIVITY MONITORS PROVIDING ALARM BUT NOT PROVIDING AUTOMATIC TERMINATION OF RELEASE

a. Circulating Water Reservoir Decant Line Dl1-N402 1 111

3. FLOW RATE.MEASUREMENT DEVICES

a. Liquid Radwaste Effluent Line G1I-R703 1 112 TABLE NOTATION The circulating water reservoir decant line flow rate monitor has been removed. The flow rate in this decant line is now measured using certified pump performance curves for the circulating water reservoir decant pumps, together with readings from pump discharge pressure gauges and reservoir level indication.

FERMI 2 ODCM - TRM VOLUME II 3-6 Rev. 14

TABLE 3.3.7.11-1 (Continued)

TABLE NOTATIONS ACTION 110 - With the number of channels FUNCTIONALLY CAPABLE less than that required by the Minimum Channels FUNCTIONALLY CAPABLE requirement, effluent releases from this pathway may continue provided that prior to initiating a release:

a. At least two independent samples are analyzed in accordance with Surveillance Requirement 4.11.1.1.1, and

b. At least two technically qualified individuals independently verify the release rate calculations and discharge line valving (one technically qualified individual can be the preparer of the calculation, the other independently reviews the release rate calculations to verify accuracy);

Otherwise, suspend release of radioactive effluents via this pathway.

ACTION 111 - With the number of channels FUNCTIONALLY CAPABLE less than the

,Minimum Channels FUNCTIONALLY CAPABLE requirement, radioactive effluent releases via this pathway may continue provided that grab samples are collected and analyzed at least once per 12 hours1.388889e-4 days 0.00333 hours 1.984127e-5 weeks 4.566e-6 months for gross radioactivity (beta or gamma) at a lower limit of detection of at least 10-7 microcurie/ml, for Cs-1 37. Otherwise, suspend release of radioactive effluents via this pathway. If radioactive effluent releases are not in progress, i.e., if no Waste Sample Tank (or other tank containing radioactive liquid) is being released and the circulating water is not contaminated as shown by the most recent circulating water sample(s),

this sampling requirement does not apply.

ACTION 112 - With the number of channels FUNCTIONALLY CAPABLE less than required by the Minimum Channels FUNCTIONALLY CAPABLE requirement, radioactive effluent releases via this pathway may continue provided the flow rate is estimated at least once per 4 hours4.62963e-5 days 0.00111 hours 6.613757e-6 weeks 1.522e-6 months during actual releases. Otherwise, suspend release of radioactive effluents via this pathway. If radioactive effluent releases are not in progress, i.e., if no Waste Sample Tank (or other tank containing radioactive liquid) is being released, this requirement does not apply.

FERMI 2 ODCM - TRM VOLUME II 3-7 Rev. 14

TABLE 4.3.7.11-1 k.

RADIOACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION SURVEILLANCE REQUIREMENTS Instrument Channel Source C'hannel Channel Check Check Calibration FunctionalTest

1. GROSS RADIOACTIVITY MONITORS PROVIDING ALARM AND AUTOMATIC TERMINATION OF RELEASE

a. Liquid Radwaste Effluent Line P P R(3) Q(1) (2)

2. GROSS BETA OR GAMMA RADIOACTIVITY MONITORS PROVIDING ALARM BUT NOT PROVIDING AUTOMATIC TERMINATION OF RELEASE

a. Circulating Water Reservoir Decant Line D M R(3) Q(5)

D11 -N402 S

3. FLOW RATE MEASUREMENT DEVICES (4)

a. Liquid Radwaste Effluent Line D(4) N.A. R Q FERMI 2 ODCM - TRM VOLUME II 3-8 Rev. 14 I/

TABLE 4.3.7.11-1 (Continued)

TABLE NOTATIONS (1) The CHANNEL FUNCTIONAL TEST shall also demonstrate that automatic isolation of this pathway occurs if any of the following conditions exists:

1. Instrument indicates measured levels above the alarm/trip setpoint.

2. Circuit failure.

(2) The CHANNEL FUNCTIONAL TEST shall also demonstrate that control room alarm annunciation occurs if any of the following conditions exists:

1. Instrument indicates measured levels above the alarm setpoint.

2. Circuit failure.

3. Instrument indicates a downscale failure.

4. Instrument controls not set in operate mode.

(3) The initial CHANNEL CALIBRATION shall be performed using National Institute of Standards and Technology traceable sources. These standards shall permit calibrating the system over the range of energy and measurement expected during normal operation and anticipated operational occurrences. For subsequent CHANNEL CALIBRATION, sources that have been related to the initial calibration or are National Institute of Standards and Technology traceable shall be used.

(4) CHANNEL CHECK shall consist of verifying indication of flow during periods of release.

CHANNEL CHECK shall be made at least once per 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months on days on which continuous, periodic, or batch releases are made.

(5) The CHANNEL FUNCTIONAL TEST shall also demonstrate that control room alarm annunciation occurs if any of the following conditions exists:

1. Instrument indicates measured levels above the alarm setpoint.

2. Circuit failure.

3. Instrument indicates a downscale failure.

FERMI 2 ODCM - TRM VOLUME II 3-9 Rev. 13

INSTRUMENTATION RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION CONTROLS 3.3.7.12 The radioactive gaseous effluent monitoring instrumentation channels shown in Table 3.3.7.12-1 shall be FUNCTIONALLY CAPABLE with their alarm/trip setpoints set to ensure that the limits of Control 3.11.2.1 are not exceeded. The alarm/trip setpoints of these channels, with the exception of the offgas monitoring system, shall be determined and adjusted in accordance with the methodology and parameters in the ODCM.

APPLICABILITY: Actions a and b: As shown in Table 3.3.7.12-1 Actions c and d: At all times ACTION:

a; With a radioactive gaseous effluent monitoring instrumentation channel alarm/trip setpoint less conservative than required by the above Control, immediately suspend the release of radioactive gaseous effluents monitored by the affected channel, or declare the channel not FUNCTIONALLY CAPABLE, or change the setpoint so it is acceptably conservative.

b. With less than the minimum number of radioactive gaseous effluent monitoring instrumentation channels FUNCTIONALLY CAPABLE, take the ACTION shown in Table 3.3.7.12-1.

c. Restore radioactive gaseous effluent monitoring instrumentation which is not FUNCTIONALLY CAPABLE to FUNCTIONALLY CAPABLE status within 30 days and, if unsuccessful, explain why this condition was not corrected in a timely manner in the next Annual Radioactive Effluent Release Report.

d. The provisions of Controls 3.0.3 and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS 4.3.7.12 Each radioactive gaseouseffluent monitoring instrumentation channel shall be demonstrated FUNCTIONALLY CAPABLE by performance of the CHANNEL CHECK, CHANNEL CALIBRATION, and CHANNEL FUNCTIONAL TEST operations at the frequencies shown in Table 4.3.7.12-1.

Note: Page content was last changed with ODCM Revision 15. 1 L./q FERMI 20ODCM - TRM VOLUME II 3-10 R-ev.-f

TABLE 3.3.7.12-1 RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION

'Minimum Channels Instrument Functionalfly Applicability Action

_____________________________________ Capable _____________

1I. REACTOR BUILDING EXHAUST PLENUM EFFLUENT i MONITORING SYSTEM

a. Low Range Noble Gas Activity Monitor - Providing Alarm 1121

b. Iodine Sampler 1*122

c. Particulate Sampler 1 I 122

d. Sampler Flow Rate Monitor 1 123

12. OFFGAS MONITORING SYSTEM (At the 2.2 minute delay piping)

a. Noble Gas Activity Monitor - Providing Alarm 1 1126

3. STANDBY GAS TREATMENT SYSTEM

a. Low Range Noble Gas Activity Monitor -Providing Alarm # 125

b. Iodine Sampler 1 122

c. Particulate Sampler 1 122 d, Sampler Flow Rate Monitor 1 123

14. TURBINE BLDG. VENTILATION MONITORING SYSTEM

a. Low Range Noble GasActivity Monitor -Providing Alarm 1121

b. Iodine Sampler 1122

c. Particulate Sampler 1*122

d. Sampler Flow Rate Monitor 1123 TABLE NOTATIONS

At all times.

- During operation of the main condenser air. ejector.

During operation of the standby gas treatment system.

FERMI 2 00CM - TRM VOLUME 11 3-11 Rev. 13

TABLE 3.3.7.12-1 (Continued)

(

RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION Minimum Channels Instrument Functionally Applicability Action

15. RADWASTE BUILDING VENTILATION MONITORING Capable _

I SYSTEM

a. Low Range Noble Gas Activity Monitor - Providing Alarm 1 121

b. Iodine Sampler 1 122

c. Particulate Sampler 1

122

d. Sampler Flow Rate Monitor 1

123

6. ONSITE STORAGE BUILDING VENTILATION EXHAUST RADIATION MONITOR

a. Low Range Noble Gas Activity Monitor - Providing Alarm 1 121

b. Iodine Sampler 1 122

c. Particulate Sampler 1 122

d. Sampler Flow Rate Monitor 1 123 TABLE NOTATIONS

At all times.

FERMI 2 ODCM - TRM VOLUME II 3-12 Rev. 13

(

TABLE 3.3.7.12-1 (Continued)

ACTION STATEMENTS ACTION 121 - With the number of channels FUNCTIONALLY CAPABLE less than required by the Minimum Channels FUNCTIONALLY CAPABLE requirement, effluent releases via this pathway may continue provided grab samples are taken at least once per 9 hours1.041667e-4 days 0.0025 hours 1.488095e-5 weeks 3.4245e-6 months and these samples are analyzed for gross activity within 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months , or, ifvalid monitor indication of noble gas concentration is available, that noble gas concentration readings are recorded at least once per 9 hours1.041667e-4 days 0.0025 hours 1.488095e-5 weeks 3.4245e-6 months . Otherwise, suspend release of radioactive effluents via this pathway.

ACTION 122- With the number of channels FUNCTIONALLY CAPABLE one less than required by the Minimum Channels FUNCTIONALLY CAPABLE requirement, effluent releases via this pathway may continue provided that within 8 hours9.259259e-5 days 0.00222 hours 1.322751e-5 weeks 3.044e-6 months samples are continuously collected with auxiliary sampling equipment as required in Table 4.11.2.1.2-1.

ACTION 123 - With the number of channels FUNCTIONALLY CAPABLE less than required by the Minimum Channels FUNCTIONALLY CAPABLE requirement, effluent releases via this pathway may continue provided the flow rate is estimated at least once per 9 hours1.041667e-4 days 0.0025 hours 1.488095e-5 weeks 3.4245e-6 months . Otherwise, suspend release of radioactive effluents via this pathway.

ACTION 124 - Not used.

ACTION 125 - With the number of channels FUNCTIONALLY CAPABLE less than required by the Minimum Channels FUNCTIONALLY CAPABLE requirement, effluent releases via this pathway may continue provided grab samples are taken at least once per 9 hours1.041667e-4 days 0.0025 hours 1.488095e-5 weeks 3.4245e-6 months and these samples are analyzed for gross activity within 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months , or, if valid monitor indication of noble gas concentration is available, that noble gas concentration readings are recorded at least once per 9 hours1.041667e-4 days 0.0025 hours 1.488095e-5 weeks 3.4245e-6 months . Otherwise, suspend release of radioactive effluents via this pathway.

ACTION 126- With the number of channels FUNCTIONALLY CAPABLE less than required by the Minimum Channels FUNCTIONALLY CAPABLE requirement, releases via this pathway to the environment may continue for up to 7 days provided that:

a. The offgas system is not bypassed, and

b. The.reactor building exhaust plenum noble gas effluent (downstream) monitor is FUNCTIONALLY CABAPLE; Otherwise, be in at least HOT STANDBY within 12 hours1.388889e-4 days 0.00333 hours 1.984127e-5 weeks 4.566e-6 months .

. -Nete>-.-Page e was last- ehae

-ntcnt with-ODGM-Revisien1-6:

FERMI 2 ODCM - TRM VOLUME II 3-13 Rev. 18

TABLE 4.3.7.12-1

(

RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION SURVEILLANCE REQUIREMENTS Instrument

11. REACTOR BUILDING EXHAUST PLENUM

a. Low Range Noble Gas Activity Monitor - D jM R(2) Q(1)

Providing Alarm

b. Iodine Sampler W N.A. N.A. N.A.

c. Particulate Sampler W NýA. N.A. N.A

d. Sampler Flow Rate Monitor D N.A. R Q

2. OFFGAS MONITORING SYSTEM (At the 2.2 minute delay piping)

a. Noble Gas Activity Monitor D M R(2) Q(1)

3. STANDBY GAS TREATMENT MONITORING SYSTEM

a. Low Range Noble Gas Activity Monitor D M W(1) #

NA.

b. Iodine Sampler W N.A. N.A. #

N.A.

c. Particulate Sampler W N.A. N.A. #

d. Sampler Flow Rate Monitor D N.A. R Q

4. TURBINE BLDG. VENTILATION MONITORING SYSTEM

a. Low Range Noble Gas Activity Monitor D M R(2) Q(4)

b. Iodine Sampler W N.A. N.A. NýA.

c. Particulate Sampler W N.A. N.A. N A.

d. Sampler Flow Rate Monitor D N.A. R Q

_________ ___________ I.

(

FERMI 2 ODCM - TRM VOLUME II 3-14 Rev. 13

TABLE 4.3.7.12-1 (Continued)

Ii RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION SURVEILLANCE REQUIREMENTS Channel Modes in Instrument Channel Source Channel Functional Which Check Check Calibration Test Surveillance Required I5. RADWASTE BUILDING VENTILATION MONITORING SYSTEM a Low Range Noble Gas Activity Monitor D M R(2) Q(4) *

b. Iodine Sampler W N.A. N.A. N.A.

c. -Particulate Sampler W N.A. N.A. N.A.

d. Sampler Flow Rate Monitor D N.A. R Q

6. ONSITE STORAGE BUILDING VENTILATION EXHAUST RADIATION MONITOR

a. Low Range Noble Gas Activity Monitor D M R(2) Q(1)

b. Iodine Sampler W N.A. N.A. N.A.

c. Particulate Sampler W N.A. NA. N.A. I *

d. Sampler Flow Rate Monitor D N.A. R 0

_~~~~_

_ _ '._ _ I _ _ I _ _ _ _ I1_

FERMI 2 ODCM - TRM VOLUME II 3-15 Rev. 13

TABLE 4.3.7.12-1 (Continued)

TABLE NOTATIONS At all times.

During operation of the main condenser air ejector.

During operation of the standby gas treatment system.

(1) The CHANNEL FUNCTIONAL TEST shall also demonstrate that control room alarm annunciation occurs if any of the following conditions exists:

1. Instrument indicates measured levels above the alarm setpoint.

2. Circuit failure.

3. Instrument indicates a downscale failure.

4. Instrument controls not set in operate mode (alarm or type).

(2) The initial CHANNEL CALIBRATION shall be performed using National Institute of Standards and Technology traceable sources. These standards shall permit calibrating the system over the range of energy and measurement expected during normal operation and anticipated operational occurrences. For subsequent CHANNEL CALIBRATION, sources that have been related to the initial calibration or are National Institute of Standards and Technology traceable shall be used.

(3) Not used.

(4) The CHANNEL FUNCTIONAL TEST shall also demonstrate that automatic isolation occurs on high level and that control room alarm annunciation occurs if any of the following conditions exists:

1. Instrument indicates measured levels above the alarm setpoints.

2. Circuit failure.

3. Instrument indicates a downscale failure.

4. Instrument controls not set in the operate mode (alarm or type).

FERMI 2ODCM - TRM VOLUME II 3-16 Rev. 13

3/4.11 RADIOACTIVE EFFLUENTS 3/4.11.1 LIQUID EFFLUENTS CONCENTRATION CONTROLS 3.11.1.1 The concentration of radioactive material released in liquid effluents to UNRESTRICTED AREAS (see Figure 3.0-1) shall be limited to ten times the concentration values specified in 10 CFR Part 20, Appendix B, Table 2, Column 2 for radionuclides other than dissolved or entrained noble gases. For dissolved or entrained noble gases, the concentration shall be limited to 2 x 10-4 microcuries/ml total activity.

APPLICABILITY: At all times.

ACTION:

With the concentration of radioactive material released in liquid effluents to UNRESTRICTED AREAS exceeding the above limits, immediately restore the concentration to within the above limits.

SURVEILLANCE REQUIREMENTS 4.11.1.1.1 Radioactive liquid wastes shall be sampled and analyzed according to the sampling and analysis program of Table 4.11.1.1.1-1.

4.11.1.1.2 The results of the radioactivity analyses shall be used in accordance with the methodology and parameters in the ODCM to assure that the concentrations at the point of release are maintained within the limits of Control 3.11 . 1.

FERMI 2 ODCM - TRM VOLUME II 3-17 Rev. 13

TABLE 4.11.1.1.1-1 RADIOACTIVE LIQUID WASTE SAMPLING AND ANALYSIS PROGRAM FERMI 2 ODCM - TRM VOLUME II 3-18 Rev. 14

TABLE 4.11.1.1.1-1 (Continued)

TABLE NOTATION aThe LLD is defined, for purposes of these controls, as the smallest Concentration of radioactive material in a sample that will yield a net count, above system background, that will be detected with 95% probability with only 5% probability of falsely concluding that a blank observation represents a "real" signal.

For a particular measurement system, which may include radiochemical separation:

LLD= 4.66 - sb E V 2.22 x 106 - Y

exp (- 2t)

Where:

LLD is the "a priori" lower limit of detection as defined above, as microcuries per unit mass or volume, Sb is the standard deviation of the background counting rate or of the counting rate of a blank sample as appropriate, as counts per minute, E is the counting efficiency, as counts per disintegration, V is the sample size in units of mass or volume, 2.22 x 106 is the number of disintegrations per minute per microcurie, Y is the fractional radiochemical yield, when applicable, 2 is the radioactive decay constant for the particular radionuclide, and t for plant effluents is the elapsed time between the midpoint of sample collection and time of counting.

Typical values of E, V, Y, and t should be used in the calculation.

It should be recognized that the LLD is defined as an a g[!gri (before the fact) limit representing the capability of a measurement system and not as an a posteriori (after the fact) limit for a particular measurement.

bA batch release is the discharge of liquid wastes of a discrete volume.

Prior to sampling for analyses, each batch shall be isolated, and then thoroughly mixed by a method described in the ODCM to assure representative sampling. Batch liquid discharge may be made from only one tank at a time.

FERMI 2 ODCM - TRM VOLUME II 3-19 Rev. 13

TABLE 4.11.1.1.1-1 (Continued)

TABLE NOTATION cThe principal gamma emitters for which the LLD specification applies exclusively are:

Mn-54, Fe-59, Co-58, Co-60, Zn-65, Mo-99, Cs-134, Cs-137, Ce-141, and Ce-144. This does not mean that only these nuclides are to be considered. Other peaks that are identifiable, together with those of the above nuclides, shall also be analyzed and reported in the Annual Radioactive Effluent Release Report pursuant to Control 5.9.1.8.

dThis type of composite sample is a sample composed of aliquots of pre-release samples or grab samples taken during releases, or of aliquots of composite samples so prepared, so as to represent releases taking place over a longer period of time. The volumes of these aliquots should be proportional to the volumes of the releases which they represent.

eA continuous release is the discharge of liquid wastes of a nondiscrete volume: e.g., from a volume of a system that has an input flow during the continuous release.

fVhen the circulating water system is first discovered to be contaminated, grab samples may be taken more frequently, and may be analyzed immediately. After the source of the contamination is discovered and isolated, and contamination levels are not increasing, this grab sampling and analysis frequency may be reduced to the schedule specified in the table.

FERMI 2 ODCM - TRM VOLUME II 3-20 Rev. 14

RADIOACTIVE EFFLUENTS LIQUID EFFLUENTS DOSE CONTROLS 3.11.1.2 The dose or dose commitment to a MEMBER OF THE PUBLIC from radioactive materials in liquid effluents released, from each reactor unit, to UNRESTRICTED AREAS (see Figure 3.0-1) shall be limited:

a. During any calendar quarter to less than or equal to 1.5 mrems to the total body and to less than or equal to 5 mrems to any organ, and

b. During any calendar year to less than or equal to 3 mrems to the total body and to less than or equal to 10 mrems to any organ.

APPLICABILITY: At all times.

ACTION:

a. With the calculated dose from the release of radioactive materials in liquid effluents.

exceeding any of the above limits, prepare and submit to the Commission within 30 days, pursuant to 10 CFR 50.4, a Special Report that identifies the cause(s) for exceeding the limit(s) and defines the corrective actions that have been taken to reduce the releases and the proposed corrective actions to be taken to assure that subsequent releases will be in compliance with the above limits. This Special Report shall also include (1) the results of radiological analyses of the drinking water source and (2) the radiological impact on finished drinking water supplies with regard to the requirements of 40 CFR Part 141, Safe Drinking Water Act.*

b. The provisions of Controls 3.0.3 and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS 4-11.1.2 Cumulative dose contributions from liquid effluents for the current calendar quarter and the current calendar year shall be determined in accordance with the methodology and parameters in the ODCM at least once per 31 days.

Applicable only if drinking water supply is taken from the receiving water body within 3 miles of the plant discharge.

FERMI 2 ODOM - TRM VOLUME 11 321Rv.1 3-21 Rev. 14

RADIOACTIVE EFFLUENTS LIQUID WASTE TREATMENT CONTROLS 3.11.1.3 The liquid radwaste treatment system shall be FUNCTIONALLY CAPABLE and appropriate portions of the system shall be used to reduce the radioactive materials in liquid wastes prior to their discharge when the projected doses due to the liquid effluent, from each reactor unit, to UNRESTRICTED AREAS (see Figure 3.0-1) would exceed 0.06 mrem to the total body or 0.2 mrem to any organ in any 31-day period.

APPLICABILITY: At all times.

ACTION:

a. With radioactive liquid waste being discharged and in excess of the above limits and any portion of the liquid radwaste treatment system not in operation, prepare and submit to the Commission within 30 days, pursuant to 10 CFR 50.4, a Special Report that includes the following information:

1. Explanation of why liquid radwaste was being discharged without complete treatment, identification of any equipment or subsystems which are not FUNCTIONALLY CAPABLE, and the reason for the not FUNCTIONALLY CAPABLE status.

2. Action(s) taken to restore the equipment which is not FUNCTIONALLY CAPABLE to FUNCTIONALLY CAPABLE status, and

3. Summary description of action(s) taken to prevent a recurrence.

b. The provisions of Controls 3.0.3 and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS 4.11.1.3.1 Doses due to liquid releases from each reactor unit to UNRESTRICTED AREAS shall be projected at least once per 31 days in accordance with the methodology and parameters in the ODCM.

4.11.1.3.2 The installed liquid radwaste treatment system shall be demonstrated FUNCTIONALLY CAPABLE by meeting Controls 3.11.1.1 and 3.11.1.2.

FERMI 2 0DCM - TRM VOLUME II 3-22 Rev. 14

RADIOACTIVE EFFLUENTS 3/4.11.2 GASEOUS EFFLUENTS DOSE RATE CONTROLS 3.11.2.1 The dose rate due to radioactive materials released in gaseous effluents from the site to areas at and beyond the SITE BOUNDARY (see Figure 3.0-1) shall be limited to the following:

a. For noble gases: Less than or equal to 500 mrems/yr to the total body and less than or equal to 3000 mrems/yr to the skin, and

b. For iodine-131, iodine-1 33, tritium, and for all radionuclides in particulate form with half-lives greater than 8 days: Less than or equal to 1500 mrems/yr to any organ.

APPLICABILITY: At all times.

ACTION:

With the dose rate(s) exceeding the above limits, immediately restore the release rate to within the above limit(s).

SURVEILLANCE REQUIREMENTS 4.11.2.1.1 The dose rate due to noble gases in gaseous effluents shall be determined to be within the above limits in accordance with the methodology and parameters in the ODCM.

4.11.2.1.2 The dose rate due to iodine-131, iodine-133, tritium, and all other radionuclides in particulate form with half-lives greater than 8 days in gaseous effluents shall be determined to be within the above limits in accordance with the methodology and parameters in the ODCM by obtaining representative samples and performing analyses in accordance with the sampling and analysis program specified in Table 4.11.2.1.2-1.

FERMI 2 ODCM - TRM VOLUME II 3-23 Rev. 13

TABLE 4.11.2.1.2-1 RADIOACTIVE GASEOUS WASTE SAMPLING AND ANALYSIS PROGRAM B. Reactor Building Exhaust Plenum Mie Mc Principal Gamma 1 x 10-4 Standby Gas Emittersb Treatment Systemh Grab Sample Mc H-3 1 x 10-6 C. Radwaste Building Principal Gamma Turbine Building M M Emittersb 1 x 10-4 Gn-Site -Storage Grab Sample M H-3 x 1b;:6 Facility D. All Release Types wg 1-131 1 x 10-12 as listed in B and C Continuousf Absorbent Sample 1-133 1 x 10-10 above. iX01 wg Principal Gamma Continuousf Particulate Sample Emittersb 1 x 10-11 (1-131, others)

Gross Alpha Q

Continuousf Composite Sr-89, Sr-90 1 x 10-11 Particulate Sample Continuousf Noble Gas Monitor Noble Gas Gross 1 x 10-6 Beta or Gamma E. Offgas Vent Pipe N.A.k N.A.k Principal Gamma 1 x 10-4 Grab Sample Emittersb FERMI 2 ODCM - TRM VOLUME II 3-24 Rev. 18

TABLE 4.11.2.1.2-1 (Continued)

TABLE NOTATION aThe LLD is defined, for purposes of these controls, as the smallest concentration of radioactive material in a sample that will yield a net count, above system background, that will be detected with 95% probability with only 5% probability of falsely concluding that a blank observation represents a "real" signal.

For a particular measurement system, which may include radiochemical separation:

LLD= 4.66 - sb E "V ° 2.22 x 106 - Y - exp (- )t)

Where:

LLD is the "a priori" lower limit of detection as defined above, as microcuries per unit mass or volume, Sb is the standard deviation of the background counting rate or of the counting rate of a blank sample as appropriate, as counts per minute, E is the counting efficiency, as counts per disintegration, V is the sample size in units of mass or volume, 2.22 x 106 is the number of disintegrations per minute per microcurie, Y is the fractional radiochemical yield, when applicable, 2 is the radioactive decay constant for the particular radionuclide, and t for plant effluents is the elapsed time between the midpoint of sample collection and time of counting.

Typical values of E, V, Y, and t should be used in the calculation.

It should be recognized that the LLD is defined as an a prior (before the fact) limit representing the capability of a measurement system and not as an a posteriori (after the fact) limit for a particular measurement.

bThe principal gamma emitters for which the LLD specification applies exclusively are the following radionuclides: Kr-87, Kr-88, Xe-133, Xe-133m, Xe-135, and Xe-138 in noble gas releases and Mn-54, Fe-59, Co-58, Co-60, Zn-65, Mo-99, 1-131, Cs-134, Cs-137, Ce-141, and Ce-144 in iodine and particulate releases. This list does not mean that only these nuclides are to be considered. Other gamma peaks that are identifiable, together with those of the above nuclides, shall also be analyzed and reported in the Annual Radioactive Effluent Release Report pursuant to Control 5.9.1.8.

FERMI 2 ODCM - TRM VOLUME II 3-25 Rev. 13

TABLE 4.11.2.1.2-1 (Continued)

TABLE NOTATION CSampling and analysis shall also be performed following shutdown, startup, or a THERMAL POWER change exceeding 15% of RATED THERMAL POWER within a 1-hour period. This requirement does not apply if the noble gas monitor shows that effluent activity has not increased more than a factor of 3.

dNot used.

eTritium grab samples shall be taken at least once per 7 days from the ventilation exhaust from the spent fuel pool area, whenever spent fuel is in the spent fuel pool.

fThe ratio of the sample flow rate to the sampled stream flow rate shall be known for the time period covered by each dose or dose rate calculation made in accordance with Controls 3.11.2.1, 3.11.2.2, and 3.11.2.3.

gSamples shall be. changed at least once per 7 days and analyses shall be completed within 48 hours5.555556e-4 days 0.0133 hours 7.936508e-5 weeks 1.8264e-5 months after changing, or after removal from sampler. Sampling shall also be performed at least once per 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months for at least 3 days following each shutdown, startup or THERMAL POWER change exceeding 15% of RATED THERMAL POWER in 1 hour1.157407e-5 days 2.777778e-4 hours 1.653439e-6 weeks 3.805e-7 months , and analyses shall be completed within 48 hours5.555556e-4 days 0.0133 hours 7.936508e-5 weeks 1.8264e-5 months of changing, at any release point at which the noble gas monitor shows that effluent activity has increased more than a factor of 3.

When samples collected for 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months are analyzed, the corresponding LLDs may be increased by a factor of 10. When samples collected for periods between 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months and 7 days are analyzed, the corresponding LLDs may be increased by a factor equal to the normal weekly sample volume divided by the volume of the sample in question.

hRequired when the SGTS is in operation.

iln MODES 1, 2, 3, and 4, the applicable portion of primary containment shall be sampled and analyzed within 8 hours9.259259e-5 days 0.00222 hours 1.322751e-5 weeks 3.044e-6 months prior to the start of any PURGING.

JIln MODES 1, 2, 3, and 4, when the primary containment atmosphere radiation monitoring system is declared not FUNCTIONALLY CAPABLE or is in alarm condition, the applicable portion of primary containment shall be sampled and analyzed within 8 hours9.259259e-5 days 0.00222 hours 1.322751e-5 weeks 3.044e-6 months prior to the start of any VENTING or PURGING and at least once per 12 hours1.388889e-4 days 0.00333 hours 1.984127e-5 weeks 4.566e-6 months during VENTING or PURGING through other than SGTS.

kOffgas Vent Pipe sampling is performed as directed by Radiation Protection to supplement Reactor Building Exhaust Plenum monthly grab sampling. The Offgas Vent Pipe sample point is upstream of the Reactor Building Exhaust Plenum.

FERMI 2 ODCM - TRM VOLUME II 3-26 Rev. 18

RADIOACTIVE EFFLUENTS GASEOUS EFFLUENTS DOSE - NOBLE GASES CONTROLS 3.11.2.2 The air dose due to noble gases released in gaseous effluents, from each reactor unit, to areas at and beyond the SITE BOUNDARY (see Figure 3.0-1) shall be limited to the following:

a. During any calendar quarter: Less than or equal to 5 mrads for gamma radiation and less than or equal to 10 mrads for beta radiation and,

b. During any calendar year: Less than or equal to 10 mrads for gamma radiation and less than or equal to 20 mrads for beta radiation.

APPLICABILITY: At all times.

ACTION:

With the calculated air dose from radioactive noble gases in gaseous effluents exceeding any of the above limits, prepare and submit to the Commission within 30 days, pursuant to 10 CFR 50.4, a Special Report that identifies the corrective actions that have been taken to reduce the releases and the proposed corrective actions to be taken to assure that subsequent releases will be in compliance with the above limits.

b. The provisions of Controls 3.0.3 and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS 4.11.2.2 Cumulative dose contributions for the current calendar quarter and current calendar year for noble gases shall be determined in accordance with the methodology and parameters in the ODCM at least once per 31 days.

FERMI 2 ODCM - TRM VOLUME II 3-27 Rev. 14

RADIOACTIVE EFFLUENTS GASEOUS EFFLUENTS DOSE - IODINE-131, IODINE-133, TRITIUM, AND RADIONUCLIDES IN PARTICULATE FORM CONTROLS 3-11.2.3 The dose to a MEMBER OF THE PUBLIC from iodine-131, iodine-133, tritium, and all radionuclides in particulate form with.half-lives greater than 8 days in gaseous effluents released, from each reactor unit, to areas at and beyond the SITE BOUNDARY (see Figure 3.0-1) shall be limited to the following:

a. During any calendar quarter: Less than or equal to 7.5 mrems to any organ and,

b. During any calendar year: Less than or equal to 15 mrems to any organ.

APPLICABILITY: At all times.

ACTION:

a. With the calculated dose from the release of iodine-1 31, iodine-1 33, tritium, and radionuclides in particulate form with half-lives greater than 8 days, in gaseous effluents exceeding any of the above limits, prepare and submit to the Commission within 30 days, pursuant to 10 CFR 50.4, a Special Report that identifies the cause(s) for exceeding the limit and defines the corrective actions that have been taken to reduce the releases and the proposed corrective actions to be taken to assure that subsequent releases will be in compliance with the above limits.

b. The provisions of Controls 3.0.3 and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS 4.11.2.3 Cumulative dose contributions for the current calendar quarter and current calendar year for iodine-1 31, iodine-1 33, tritium, and radionuclides in particulate form with half-lives greater than 8 days shall be determined in accordance with the methodology and parameters in the ODCM at least once per 31 days.

FERMI 2 ODCM - TRM VOLUME II 3-28 Rev. 14

RADIOACTIVE EFFLUENTS OFF-GAS TREATMENT SYSTEM CONTROLS 3.11.2.4 The OFF-GAS TREATMENT SYSTEM shall be FUNCTIONALLY CAPABLE and shall be in operation.

APPLICABILITY: Whenever the main condenser steam jet air ejectors are in operation.

ACTION:

With the OFF-GAS TREATMENT SYSTEM not FUNCTIONALLY CAPABLE for more than 7 days, prepare and submit to the commission within 30 days, pursuant to 1ý0 CFR 50.4, a Special Report that includes the following information:

1. Identification of the equipment or subsystems which are not FUNCTIONALLY CAPABLE and the reason for the not FUNCTIONALLY CAPABLE status,

2. Action(s) taken to restore the equipment which is not FUNCTIONALLY CAPABLE to FUNCTIONALLY CAPABLE status, and

3. Summary description of action(s) taken to prevent a recurrence.

b. The provisions of Controls 3.0.3 and 3.0.4 are not applicable.

c. The provisions of Control 4.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS 4.11.2.4 The OFF-GAS TREATMENT SYSTEM shall be demonstrated FUNCTIONALLY CAPABLE by meeting Controls 3.11.2.1, 3.11.2.2, and 3.11.2.3.

FERMI 2 ODCM - TRM VOLUME 11 32 3-29 e.1 14 Rev.

RADIOACTIVE EFFLUENTS VENTILATION EXHAUST TREATMENT SYSTEM CONTROLS 3111.2.5 The VENTILATION EXHAUST TREATMENT SYSTEM as described in the ODOM shall be FUNCTIONALLY CAPABLE and appropriate portions of the system shall be used to reduce radioactive materials in gaseous waste prior to their discharge when the projected doses due to gaseous effluent releases from the site to UNRESTRICTED AREAS (see Figure 3.0-1) would exceed 0.3 mrem to any organ in any 31-day period.

APPLICABILITY: At all times.

ACTION:

With radioactive gaseous waste being discharged in excess of the above limits and any portion of the VENTILATION EXHAUST TREATMENT SYSTEM not in operation, prepare and submit to the Commission within 30 days, pursuant to 10 CFR 50.4, a Special Report that includes the following information:

1. Identification of any equipment or subsystems which are not FUNCTIONALLY CAPABLE and the reason for the not FUNCTIONALLY CAPABLE status.

2. Action(s) taken to restore the equipment which is not FUNCTIONALLY CAPABLE to FUNCTIONALLY CAPABLE status, and

3. Summary description of action(s) taken to prevent a recurrence.

b. The provisions of Controls 3.0.3 and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS 4.11.2.5.1 Doses due to gaseous releases from the site shall be projected at least once per 31 days in accordance with the methodology and parameters in the ODOM, when any portion of the VENTILATION EXHAUST TREATMENT SYSTEM is not in use.

4.11.2.5.2 The VENTILATION EXHAUST TREATMENT SYSTEM shall be demonstrated FUNCTIONALLY CAPABLE by meeting Controls 3.11.2.1, 3.11.2.2, and 3.11.2.3.

FERMI 2 ODCM - TRM VOLUME If -0Re.1 3-30 Rev. 14

RADIOACTIVE EFFLUENTS VENTING OR PURGING CONTROLS 3.11.2.8 VENTING or PURGING of the primary containment shall be through the standby gas treatment system or the reactor building ventilation system.

APPLICABILITY: MODES 1, 2, 3, and 4 ACTION:

a. With the requirements of the above control not satisfied, suspend all VENTING or PURGING of the primary containment.

b. The provision of Controls 3.0.3 and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS 4.11.2.8.1 The applicable portion of primary containment shall be sampled and analyzed per Table 4.11.2.1.2-1 of Control 3.11.2.1 within 8 hours9.259259e-5 days 0.00222 hours 1.322751e-5 weeks 3.044e-6 months prior to the start of any PURGING.

4.11.2.8.2 If the primary containment radiation monitoring system is not FUNCTIONALLY CAPABLE or is in alarm condition, the applicable portion of primary containment shall be sampled and analyzed per Table 4.11.2.1 .2-1 of Control 3.11.2.1 within 8 hours9.259259e-5 days 0.00222 hours 1.322751e-5 weeks 3.044e-6 months prior to the start of and at least once per 12 hours1.388889e-4 days 0.00333 hours 1.984127e-5 weeks 4.566e-6 months during VENTING or PURGING of primary containment through other than the standby gas treatment system.

4.11.2.8.3 The primary containment shall be determined to be aligned for VENTING or PURGING through the standby gas treatment system or the reactor building ventilation system within 4 hours4.62963e-5 days 0.00111 hours 6.613757e-6 weeks 1.522e-6 months prior to start of and at least once per 12 hours1.388889e-4 days 0.00333 hours 1.984127e-5 weeks 4.566e-6 months during VENTING or PURGING of the containment.

4.11.2.8.4 Prior to use of the vent/purge system through the standby gas treatment system assure that:

a. Both standby gas treatment system trains are FUNCTIONALLY CAPABLE whenever the vent/purge system is in use, and

b. Whenever the vent/purge system is in use during MODE 1 or 2 or 3, only one of the standby gas treatment system trains may be used.

4.11.2.8.5 Prior to VENTING or PURGING, assure that at least one of the following monitors is FUNCTIONALLY CAPABLE: the primary containment atmosphere radiation monitor, the reactor building ventilation exhaust radiation monitor (at least one division), or the SPING monitor corresponding to the. release path .(the reactor building exhaust plenum radiation monitor or the standby gas treatment system radiation monitor, Division 1 or 2).

FERMI 200DCM - TRM VOLUME 11 3-31 Rev. 13

RADIOACTIVE EFFLUENTS 3/4.11.4 TOTAL DOSE CONTROLS 3.11.4 The annual (calendar year) dose or dose commitment to any member of the public (as defined in 40 CFR Part 190) due to releases of radioactivity and to radiation from uranium fuel cycle sources shall be limited to less than or equal to 25 mrems to the total body or any organ, except the thyroid, which shall be limited to less than or equal to 75 mrems.

APPLICABILITY: At all times.

ACTION:

a. With the calculated doses from the release of radioactive materials in liquid or gaseous effluents exceeding twice the limits of Controls 3.11.1.2a., 3.11.1.2b.,

3.11.2.2a., 3.11.2.2b., 3.11.2.3a., or 3.11.2.3b., calculations should be made including direct radiation contributions from the reactor units and from outside storage tanks to determine whether the above limits of Control 3.11.4 have been exceeded. If such is the case, prepare and submit to the Commission within 30 days, pursuant to 10 CFR 50.4, a Special Report that defines the corrective action to be taken to reduce subsequent releases to prevent recurrence of exceeding the above limits and includes the schedule for achieving conformance with the above limits. This Special Report, as defined in 10 CFR 20.2203, shall include an analysis that estimates the radiation exposure (dose) to a member of the public from uranium fuel cycle sources, including all effluent pathways and direct radiation, for the calendar year that includes the release(s) covered by this report. It shall also describe levels of radiation and concentrations of radioactive material involved, and the cause of the exposure levels or concentrations. If the estimated dose(s) exceeds the above limits, and if the release condition resulting in violation of 40 CFR Part 190 has not already been corrected, the Special Report shall include a request for a variance in accordance with the provisions of 40 CFR Part 190. Submittal of the report is considered a timely request, and a variance is granted until staff action on the request is complete.

b. The provisions of Controls 3.0.3 and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS 4.11.4.1 Cumulative dose contributions from liquid and gaseous effluents shall be determined in accordance with Controls 4.11.1.2, 4.11.2.2, and 4.11.2.3, and in accordance with the methodology and parameters in the ODCM.

4.11.4.2 Cumulative dose contributions from direct radiation from the reactor units and from outside storage tanks shall be determined in accordance with the methodology and parameters in the ODCM. This requirement is applicable only under conditions set forth in Control 3.11.4, ACTION a.

Note: Page content was last changed with O DCM Revision 16.

FERMI 2 ODCM - TRM VOLUME II 3-32 Rev. 18

3/4.12 RADIOLOGICAL ENVIRONMENTAL MONITORING 314.12.1 MONITORING PROGRAM CONTROLS 3.12.1 The radiological environmental monitoring program shall be conducted as specified in Table 3.12.1-1.

APPLICABILITY: At all times.

ACTION:

a. With the radiological environmental monitoring program not being conducted as specified in Table 3.12.1-1, prepare and submit to the Commission, in the Annual Radiological Environmental Operating Report required by Control 5.9.1.7, a description of the reasons for not conducting the program as required and the plans for preventing a recurrence.

With the level 6f f~dibg-tivity 89 the regult of plant effluents in an environmental sampling medium at a specified location exceeding the reporting levels of Table 3.12.1-2 when, averaged over any calendar quarter, prepare and submit to the Commission within 30 days, pursuant to 10 CFR 50.4, a Special Report that identifies the cause(s) for exceeding the limit(s) and defines the corrective actions to be taken to reduce radioactive effluents so that the potential annual dose* to A MEMBER OF THE PUBLIC is less than the calendar year limits of Controls 3.11.1.2, 3.11.2.2, and 3.11.2.3. When more than one of'-the radionuclides in Table 3.12.1-2 are detected in the sampling medium, this report shall be submitted if:

concentration (1) + concentration (2) + ... > 1.0 reporting level (1) reporting level (2)

b. When radionuclides other than those in Table 3.12.1-2 are detected and are the result of plant effluents, this report shall be submitted if the potential annual dose* to A MEMBER OF THE PUBLIC from all radionuclides is equal to or greater than the calendar year limits of Controls 3.11.1.2, 3.11.2.2, and 3.11.2.3. This report is not required if the measured level of radioactivity was not the result of plant effluents; however, in such an event, the condition shall be reported and described in the Annual Radiological Environmental Operating Report pursuant to Control 5.9.1.7.

The methodology used to estimate the potential annual dose to a MEMBER OF THE PUBLIC shall be indicated in this report.

Note: Page content was last changed with ODCM Revision 16.

FERMI 2 ODCM - TRM VOLUME 11 3-33 Rev. 18

RADIOLOGICAL ENVIRONMENTAL MONITORING CONTROLS (Continued)

c. With milk or fresh leafy vegetable samples unavailable from one or more of the sample locations required by Table 3.12.1-1, identify specific locations for obtaining replacement samples and add them to the radiological environmental monitoring program within 30 days. The specific locations from which samples were unavailable may then be deleted from the monitoring program. Pursuant to Control 5.9.1.8, identify the cause of the unavailability of samples and identify the new location(s) for obtaining replacement samples in the next Annual Radioactive Effluent Release Report pursuant to Control 5.9.1.8 and also include in the report a revised table for the ODCM reflecting the new location(s).

d. The provisions of Controls 3.0.3.and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS 4.12.1 The radiological environmental monitoring samples shall be collected pursuant to Table 3.12.1-1 from the specific locations given in the table in the ODCM, and shall be analyzed pursuant to the requirements of Table 3.12.1-1 and the detection capabilities required by Table 4.12.1-1.

FERMI 2 ODCM - TRM VOLUME II 3-34 Rev. 13

TABLE 3.12.1-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

1. DIRECT RADIATIONb 67 routine monitoring stations, Quarterly Gamma dose quarterly.

with two or more dosimeters placed as follows: 1) an inner ring of stations in the general area of the SITE BOUNDARY and additional rings at approximately 2, 5, and 10 miles, with a station in at least every other meteorological sector for each ring with the exception of those sectors over Lake Erie.

The balance of the stations, 8, should be placed in special interest areas such as population centers, nearby residences, schools, and in 2 or 3 areas to serve as control stations.

2. AIRBORNE Samples from 5 locations. Continuous sampler Radioiodine Canister:

Radioiodine and operation with sample 1-131 analysis weekly.

Particulates a. 3 samples from close to the collection weekly, or 3 SITE BOUNDARY more frequently if Particulate Sampler:

locations, in different sectors, required by dust Gross beta radioactivity of the highest calculated loading. analysis following filter annual average ground level change:d X/Q.

Gzamma isotopic I ,

b. 1 sample from the vicinity of a community having the analysise of composite highest calculated annual (by location) quarterly.

average ground level X/Q.

c. 1 sample from a control location, as for example 15-30 km distant and in the least prevalent wind directionc.

Note: Page content was last changed with ODCM Revision 15. 2. o FERMI 2 ODCM - TRM VOLUME II 3-35 Rev. 18

TABLE 3.12.1-1 (Continued)

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM WATERBORNE

a. Surfacef a. 1 sample upstream. Composite sample Gamma isotopic b, 1 sample downstream. over 1-month periodg analysise monthly.

Composite for tritium analysis quarterly.

b. Ground Samples from 1 or 2 sources only Quarterly Gamma isotopice and I if likely to be affectedh. tritium analysis quarterly.

c. Drinking

a. I sample of each of 1 to 3 of Composite sample 1-131 analysis on each the nearest water supplies composite when the over 2-week periodg that could be affected by its dose calculated for the when 1-131 analysis is discharge. consumption of the performed, monthly water is greater than 1 composite otherwise.

b. 1 sample from a control mrem per year.i location. Composite for gross beta and gamma isotopic analysese monthly. Composite for tritium analysis quarterly.

d. Sediment from Semiannually shoreline 1 sample from downstream area Gamma isotopic with existing or potential recreational value. analysise semiannually.

FERMI 2 ODCM - TRM VOLUME II 3-36 Rev. 13

TABLE 3.12.1-1 (Continued)

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

4. INGESTION

a. Milk a. Samples from milking Semimonthly when Gamma isotopice and animals in 3 locations within animals are on 1-131 analysis 5 km distance having the pasture, monthly at semimonthly when highest dose potential. If other times. animals are on pasture; there are none, then, 1 monthly at other times.

sample from milking animals in each of 3 areas between 5 to 8 km distant where doses are calculated to be greater than 1 mrem per yri.

b. 1 sample from milking animals at a control location 15-30 km distant and in the least prevalent wind direction.

a. 1 sample of each Sample in season, or Gamma isotopic

b. Fish and commercially and semiannually if they are not seasonal. analysise on edible Invertebrates recreationally important portions.

species in vicinity of plant discharge area.

b. 1 sample of same species in areas not influenced by plant discharge.

a. 1 sample of each principal At time of harvesti. Gamma isotopic

c. Food Products class of food products from analysese on edible any area that is irrigated by portions.

water in which liquid plant wastes have been discharged.

b. Samples of 3 different kinds Monthly when Gamma isotopice and of broad leaf vegetation available. 1-131 analysis.

grown nearest each of two different offsite locations of highest predicted annual average level D/Q if locations are available and milk sampling is not performed.

Monthly when Gamma isotopice and

c. 1 sample of each of the available. 1-131 analysis.

similar broadleaf vegetation grown 15-30 km distant in the least prevalent wind direction if milk sampling is not Derformed.

Note: Page content was last changed with ODCM Revision 16.

FERMI 2 ODCM - TRM VOLUME II 3-37 Rev. 18 '2 /07

TABLE 3.12.1-1 (Continued)

(

TABLE NOTATIONS aSpecific parameters of distance and direction sector from the centerline of one reactor, and additional description where pertinent, shall be provided for each and every sample location in Table 3.12.1-1 in a table in the ODCM. Refer to NUREG-0133, "Preparation of Radiological Effluent Technical Specifications for Nuclear Power Plants," October 1978, and to Radiological Assessment Branch Technical Position, Revision 1, November 1979. Deviations are permitted from the required sampling schedule if specimens are unobtainable due to hazardous conditions, seasonal unavailability, malfunction of automatic sampling equipment and other legitimate reasons. If specimens are unobtainable due to sampling equipment malfunction, every effort shall be made to complete corrective action prior to the end of the next sampling period. All deviations from the sampling schedule shall be documented in the Annual Radiological Environmental Operating Report pursuant to Control 5.9.1.7. It is recognized that, at times, it may not be possible or practicable to continue to obtain samples of the media of choice at the most desired location or time. In these instances suitable specific alternative media and locations may be chosen for the particular pathway in question and appropriate substitutions made within 30 days in the radiological environmental monitoring program. Pursuant to Control 5.9.1.8, identify the cause of the unavailability of samples for that pathway and identify the new location(s) for obtaining replacement samples in the next Annual Radioactive Effluent Release Report and also include in the report a revised table for the ODCM reflecting the new location(s).

bOne or more instruments, such as a pressurized ion chamber, for measuring and recording dose rate continuously may be used in place of, or in addition to, integrating dosimeters. For the purpose of this table, a thermoluminescent dosimeter (TLD) is considered to be one phosphor; two or more phosphors in a packet are considered as two or more dosimeters. Film badges shall not be used as dosimeters for measuring direct radiation. The frequency of analysis or readout for TLD systems will depend upon the characteristics of the specific system used and should be selected to obtain optimum dose information with minimal fading.

cThe purpose of this sample is to obtain background information. If it is not practical to establish control locations in accordance with the distance and wind direction criteria, other sites that have valid background data may be substituted.

dAirborne particulate sample filters shall be analyzed for gross beta radioactivity 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months or more after sampling to allow for radon and thoron daughter decay. If gross beta activity in air particulate samples is greater than 10 times the yearly mean of control samples, gamma isotopic analysis shall be performed on the individual samples.

eGamma isotopic analysis means the identification and quantification of gamma-emitting radionuclides that may be attributable to the effluents from the facility.

FERMI 2 ODCM - TRM VOLUME II 3-38 Rev. 13

TABLE 3.12.1-1 (Continued)

TABLE NOTATION fThe "upstream sample" shall be taken at a distance beyond significant influence of the discharge. The "downstream" sample shall be taken in an area beyond but near the mixing zone.

"Upstream" samples in an estuary must be taken far enough upstream to be beyond the plant influence.

gComposite samples should be collected with equipment (or equivalent) which is capable of collecting an aliquot at time intervals that are very short (e.g., hourly) relative to the compositing period (e.g., monthly).

hGroundwater samples shall be taken when this source is tapped for drinking or irrigation purposes in areas where the hydraulic gradient or recharge properties are suitable for contamination.

iThe dose shall be calculated for the maximum organ and age group, using the methodology and parameters in the ODCM.

JIlf harvest occurs more than once a year, sampling shall be performed during each discrete harvest. If harvest occurs continuously, sampling shall be monthly. Attention shall be paid to including samples of tuberous and root food products.

FERMI 2 ODCM - TRM VOLUME II 3-39 Rev. 13

7 TABLE 3.12.1-2 REPORTING LEVELS FOR RADIOACTIVITY CONCENTRATIONS IN ENVIRONMENTAL SAMPLES Reporting Levels Water Airborne Fish Milk Food Analysis (pCi/I) Particulateor (pCi/kg,wet) (pCi/i) Products Gases (pCi/m3 ) (pCi/kg,wet)

H-3 20,000*

Mn-54 1,000 30,000 Fe-59 400 10,000 Co-58 1,000 30,000 Co-60 300 10,000 Zn-65 300 20,000 Zr-Nb-95 400 1-131 2 0.9 3 100

, Cs-134 30 10 1.000 60 1,000 i Cs-1 37 50 20 2,000 70 2,000 Ba-La-140 200 300

For drinking water samples. This is 40 CFR Part 141 value.

FERMI 2 ODCM - TRM VOLUME II 3-40 Rev. 13 1

TABLE 4.12.1-1 DETECTION CAPABILITIES FOR ENVIRONMENTAL SAMPLE ANALYSIS a LOWER LIMIT OF DETECTION (LLD)b,c Water Airborne Fish Milk Food Sediment (pCi/I) Particulateor (p Cl/kg, wet) (pCi/I) Products Analysis (pCi/kg, dry)

Gases (pCi/m3 ) (pCl/kg, wet) gross beta 4 0.01 H-3 2000 i Mn-54 15 130 Fe-59 30 260 Co-58;60 15 130 Zn-65 30 260 Zr-Nb-95 15 1-131 id 0.07 1 60 Cs-134 15 0.05 130 15 60 150 Cs-137 18 0.06 150 18 80 180 Ba-La-140 15 15 FERMI 2 ODCM - TRM VOLUME II 3-41 Rev. 13 1

TABLE 4.12.1-1 (Continued)

TABLE NOTATIONS aThis list does not mean that only these nuclides are to be considered. Other peaks that are identifiable, together with those of the above nuclides, shall also be analyzed and reported in the Annual Radiological Environmental Operating Report pursuant to Control 5.9.1.7.

bRequired detection capabilities for thermoluminescent dosimeters used for environmental measurements are given in Regulatory Guide 4.13.

cThe LLD is defined, for purposes of these Controls, as the smallest concentration of radioactive material in a sample that will yield a net count, above system background, that will be detected with 95% probability with only 5% probability of falsely concluding that a blank observation represents a "real" signal.

For a particular measurement system, which may include radiochemical separation:

LLD= 4.66 - sb EV-2.22 ,Y-exp(-2t)

Where:

LLD is the "a priori" lower limit of detection as defined above, as picocuries per unit mass or volume, Sb is the standard deviation of the background counting rate or of the counting rate of a blank sample as appropriate, as counts per minute, E is the counting efficiency, as counts per disintegration, V is the sample size in units of mass or volume, 2.22 is the number of disintegrations per minute per picocurie,

-Y is the fractional radiochemical yield, when applicable, A is the radioactive decay constant for the particular radionuclide, and t for environmental samples is the elapsed time between sample collection, or end of the sample collection period, and time of counting Typical values of E, V, Y, and t should be used in the calculation.

FERMI 2 ODCM - TRM VOLUME II 3-42 Rev. 13

TABLE 4.12.1-1 (Continued)

TABLE NOTATIONS It should be recognized that the LLD is defined as an -agrior (before the fact) limit representing the capability of a measurement system and not as an a posteriori (after the fact) limit for a particular measurement. Analyses shall be performed in such a manner that the stated LLDs will be achieved under routine conditions. Occasionally background fluctuations, unavoidable small sample sizes, the presence of interfering nuclides, or other uncontrollable circumstances may render these LLDs unachievable. In such cases, the contributing factors shall be identified and described in the Annual Radiological Environmental Operating Report pursuant to Control 5.9.1.7.

dLLD for drinking water samples.

FERMI 2 ODCM - TRM VOLUME !1 3-43 Rev. 13 1

RADIOLOGICAL ENVIRONMENTAL MONITORING (314.12.2 LAND USE CENSUS CONTROLS 3.12.2 A land use census shall be conducted and shall identify within a distance of 8 kmn (5 miles) the location in each of the 16 meteorological sectors of the nearest milk animal, the nearest residence and the nearest garden* of greater than 50 m2 (500 ft2 ) producing broad leaf vegetation.

APPLICABILITY: At all times.

ACTION:

a. With a land use census identifying a lacation(s) that yields a calculated dose or dose commitment greater than the values currently being calculated in Surveillance Requirement 4.11.2.3, identify the new location(s) in the next Annual Radioactive Effluent Release Report, pursuant to Control 5.9.1.8._

b. With a land use census identifying a location(s) that yields a calculated dose or dose commitment (via the same exposure pathway) 20% greater than at a location from which samples are currently being obtained in accordance with Control 3.12.1, add the new location(s) to the radiological environmental monitoring program within 30 days. The sampling location(s), excluding the control station location, having the lowest calculated dose or dose commitment(s), via the same exposure pathway, may be deleted from this monitoring program after October 31 of the year in which this land use census was conducted. Pursuant to Control 5.9.1 .8, identify the new location(s) in the next Annual Radioactive Effluent Release Report and also include in the report a revised table for the ODOM reflecting the new location(s).

c. The provisions of Control 3.0.3 and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS 4.12.2 The land use census shall be conducted during the growing season at least once per 12 months using that information that will provide the best results, such as by a door-to-door survey, visual survey, aerial survey, or by consulting local agriculture authorities. The results of the land use census shall be included in the Annual Radiological Environmental Operating Report pursuant to Control 5.9.1.7.

Broad leaf vegetation sampling of at least three different kinds of vegetation may be performed at the SITE BOUNDARY in each of two different direction sectors with the highest predicted D/Qs in lieu of the garden census. Controls for broad leaf vegetation sampling in Table 3.12.1-1, Part 4.c, shall be followed, including analysis of control samples.

FERMI 2 ODCM - TRMV VOLUME 11 3-44 Rev. 13

RADIOLOGICAL ENVIRONMENTAL MONITORING 3/4.12.3 INTERLABORATORY COMPARISON PROGRAM CONTROLS 3.12.3 Analyses shall be performed on radioactive materials supplied as part of an Interlaboratory Comparison Program which is audited periodically by Fermi 2 Quality Assurance.

APPLICABILITY: At all times.

ACTION:

a. With analyses not being performed as required above, report the corrective actions taken to prevent a recurrence to the Commission in the Annual Radiological Environmental Operating Report pursuant to Control 5.9.1.7.

b. The provisions of Controls 3.0.3 and 3.0.4 are not applicable.

SURVEILLANCE REQUIREMENTS 4.12.3 The Interlaboratory Comparison Program shall be described in the ODCM. A summary of the results obtained as part of the above required Inter-laboratory Comparison Program shall be included in the Annual Radiological Environmental Operating Report pursuant to Control 5.9.1.7.

FERMI 2 ODCM - TRM VOLUME II 3-45 Rev. 13

(

Figure 3.0-1: Map Defining Unrestricted Areas and Si jundary for Radioactive Gaseous and Liquid Efrfuents NORMALRADIOLOGICAL RELEASE POINTS LEGEND S GASEOUS LIOUID LIO.UIDUNRESIPICIED AREABOUNDARY

. . . . . rGASEOUS UNRESIRICTEO AREABOUNDARY GASEOUS RELEASE ELEVATIONS I. REACTORBUILDING

751 FT

2. RADWASTEBUILDING -729 F ;

3. ON-SITE STORAGEBUILDING - 676 Ff LAKE

4. URLBINEBUILDING - 7?B FT ERIE II

.ON-SITESTORAGEITUJLDING ENLARGED VIEW FERMI 20ODCM - TRM VOLUME 11 3-46 END OF SECTION 3.0 Rev. 13 I

SECTION 4.0 BASES FERMI 2 ODCM - TRM VOLUME II 4-1 Rev. 13

INSTRUMENTATION BASES 3/4.3.7.11 RADIOACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION The radioactive liquid effluent monitoring instrumentation is provided to monitor and control, as applicable, the releases of radioactive materials in liquid effluents during actual or potential releases of liquid effluents. The alarm/trip setpoints for these instruments shall be calculated and adjusted in accordance with the methodology and parameters in the ODCM to ensure that the alarm/trip will occur prior to exceeding the limits of 10 CFR Part 20. The FUNCTIONAL CAPABILITY and use of this instrumentation is consistent with the requirements of General Design Criteria 60, 63, and 64 of Appendix A to 10 CFR Part 50.

3/4.3.7.12 RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION The radioactive gaseous effluent monitoring instrumentation is provided to monitor and control, as applicable, the releases of radioactive materials in gaseous effluents during actual or potential releases of gaseous effluents. The alarm/trip setpoints for these instruments shall be calculated and adjusted in accordance with the methodology and parameters in the ODCM utilizing the system design flow rates as specified in the ODCM. This conservative method is used because the Fermi 2 design does not include flow rate measurement devices. This will ensure the alarm/trip will occur prior to exceeding the limits of 10 CFR Part 20. The FUNCTIONAL CAPABILITY and use of this instrumentation is consistent with the requirements of General Design Criteria 60, 63, and 64 of Appendix A to 10 CFR Part 50.

3/4.11.1 LIQUID EFFLUENTS 3/4.11.1.1 CONCENTRATION This control is provided to ensure that the concentration of radioactive materials released in liquid waste effluents to UNRESTRICTED-AREAS will be less than ten times the concentration levels specified in 10 CFR Part 20, Appendix B, Table 2, Column 2. This limitation provides additional assurance that the levels of radioactive materials in bodies of water in UNRESTRICTED AREAS will result in exposures within (1) the Section II.A design objectives of Appendix I, 10 CFR Part 50, to a MEMBER OF THE PUBLIC and (2) the limits of 10 CFR Part -

20.1301 to a MEMBER OF THE PUBLIC. The concentration limit for dissolved or entrained noble gases is based upon the assumption that Xe-1 35 is the controlling radioisotope and its MPC in air (submersion) was converted to an equivalent concentration in water using the methods described in International Commission on Radiological Protection (ICRP) Publication 2.

The required detection capabilities for radioactive materials in liquid waste samples are tabulated in terms of the lower limits of detection (LLDs). Detailed discussion of the LLD, and other detection limits can be found in HASL Procedure Manual, HASL-300 (revised annually),

Currie, L. A., "Limits for Qualitative Detection and Quantitative Determination - Application to Radiochemistry," Anal. Chem. 40, 586-93 (1968), and Hartwell, J. K., "Detection Limits for Radioanalytical Counting Techniques," Atlantic Richfield Hanford Company Report ARH-SA-215 (June 1975).

FERMI 2 ODCM - TRM VOLUME II 4-2 Rev. 13 1

RADIOACTIVE EFFLUENTS BASES 3/4.11.1.2 DOSE This control is provided to implement the requirements of Sections Il.A, Ill.A, and IV.A of Appendix 1, 10 CFR Part 50. The control implements the guides set forth in Section II.A of Appendix I. The ACTION statements provide the required operating flexibility and at the same time implement the guides set forth in Section IV.A of Appendix I to assure that the releases of radioactive material in liquid effluents to UNRESTRICTED AREAS will be kept "as low as is reasonably achievable." Also, for fresh water sites with drinking water supplies that can be potentially affected by plant operations, there is reasonable assurance that the operation of the facility will not result in radionuclide concentrations in the finished drinking water that are in excess of the requirements of 40 CFR Part 141. The dose calculation methodology and parameters in the ODCM implement the requirements in Section III.A of Appendix I that conformance with the guides of Appendix I be shown by calculational procedures based on models and data, such that the actual exposure of a MEMBER OF THE PUBLIC through appropriate pathways is unlikely to be substantially underestimated. The equations specified in the ODCM for calculating the doses due to the actual release rates of radioactive materials in liquid effluents are consistent with the methodology provided in Regulatory Guide 1.109, "Calculation of Annual Doses to Man from Routine Releases of Reactor Effluents for the Purpose of Evaluating Compliance with 10 CFR Part 50, Appendix I," Revision 1, October 1977 and Regulatory Guide 1.113, "Estimating Aquatic Dispersion of Effluents from Accidental and Routine Reactor Releases for the Purpose of Implementing Appendix I," April 1977.

3/4.11.1.3 LIQUID RADWASTE TREATMENT SYSTEM The FUNCTIONAL CAPABILITY of the liquid radwaste treatment system ensures that this system will be available for use whenever liquid effluents require treatment prior to their release to the environment. The requirement that the appropriate portions of this system be used, when specified, provides assurance that the releases of radioactive materials in liquid effluents will be kept "as low as is reasonably achievable". This specification implements the requirements of General Design Criterion 60 of Appendix A to 10 CFR Part 50 and the design objective given in Section II.D of Appendix I to 10 CFR Part 50. The specified limits governing the use of appropriate portions of the liquid radwaste treatment system were specified as a suitable fraction of the dose design objectives set forth in Section II.A of Appendix I, 10CFR Part 50, for liquid effluents.

3/4,11.2 GASEOUS EFFLUENTS 3/4.11.2.1 DOSE RATE This control is provided to ensure that the dose to individual MEMBERS OF THE PUBLIC from gaseous effluents from all units on the site will be within the limits of 10 CFR Part 20.1301.

FERMI 2 ODCM - TRM VOLUME II 4-3 Rev. 13

RADIOACTIVE EFFLUENTS BASES 3/4.11.2.1 DOSE RATE (Continued)

Although this control applies to the SITE BOUNDARY, the occupancy and exposure pathways applicable to a MEMBER OF THE PUBLIC who may at times be within the SITE BOUNDARY will usually be such that such an individual will not receive significantly greater dose due to gaseous effluents than a MEMBER OF THE PUBLIC who remains outside the SITE BOUNDARY. Examples of calculations for such MEMBERS OF THE PUBLIC, with the appropriate occupancy factors, shall be given in the ODCM. The specified dose rate limits restrict, at all times, the dose rates above background to a MEMBER OF THE PUBLIC at or beyond the SITE BOUNDARY to less than or equal to 500 mrems/year to the total body or to less than or equal to 3000 mrems/year to the skin. These dose rate limits also restrict, at all times, the thyroid dose rates above background to a child via the inhalation pathway to less than or equal to 1500 mrems/year.

The required detection capabilities for radioactive materials in gaseous waste samples are tabulated in terms of the lower limits of detection (LLDs). Detailed discussion of the LLD, and other detection limits can be found in HASL Procedures Manual, HASL-300 (revised annually),

Currie, L. A., "Limits for Qualitative Detection and Quantitative Determination - Application to Radiochemistry," Anal- Chem. 40, 586-93 (1968), and Hartwell, J. K., "Detection Limits for Radioanalytical Counting Techniques," Atlantic Richfield Hanford Company Report ARH-SA-215 (June 1975).

3/4.11.2.2 DOSE - NOBLE GASES This control is provided to implement the requirements of Sections II.B, Ill.A, and IV.A of Appendix I, 10 CFR Part 50. The control implements the guides set forth in Section 11.B of Appendix I. The ACTION statements provide the required operating flexibility and at the same time implement the guides set forth in Section IV.A of Appendix I to assure that the releases of radioactive material in gaseous effluents to UNRESTRICTED AREAS will be kept "as low as is reasonably achievable." The Surveillance Requirements implement the requirements in Section III.A of Appendix I that conformance with the guides of Appendix I be shown by calculational procedures based on models and data such that the actual exposure of a MEMBER OF THE PUBLIC through appropriate pathways is unlikely to be substantially underestimated. The dose calculation methodology and parameters established in the ODCM for calculating the doses due to the actual release rates of radioactive noble gases in gaseous effluents are consistent with the methodology provided in Regulatory Guide 1.109, "Calculation of Annual Doses to Man from Routine Releases of Reactor Effluents for the Purpose of Evaluating Compliance with 10 CFR Part 50, Appendix I," Revision 1, October 1977 and Regulatory Guide 1.111, "Methods for Estimating Atmospheric Transport and Dispersion of Gaseous Effluents in Routine Releases from Light-Water Cooled Reactors," Revision 1, July 1977. The ODCM equations provided for determining the air doses at and beyond the SITE BOUNDARY are based upon the historical average atmospheric conditions.

FERMI 2 ODCM - TRM VOLUME II 4-4 Rev. 13 1

RADIOACTIVE EFFLUENTS BASES 3/4.11.2.3 DOSE - IODINE-131, IODINE-133, TRITIUM, AND RADIONUCLIDES IN PARTICULATE FORM This control is provided to implement the requirements of Sections II.C, Ill.A, and IV.A of Appendix 1,10 CFR Part 50. The controls are the guides set forth in Section I1.C of Appendix I.

The ACTION statements provide the required operating flexibility and at the same time implement the guides set forth in Section IV.A of Appendix I to assure that the releases of radioactive materials in gaseous effluents to UNRESTRICTED AREAS will be kept "as low as is reasonably achievable." The ODCM calculational methods specified in the Surveillance Requirements implement the requirements in Section III.A of Appendix I that conformance with the guides of Appendix I be shown by calculational procedures based on models and data, such that the actual exposure of a MEMBER OF THE PUBLIC through appropriate pathways is unlikely to be substantially underestimated. The ODCM calculational methodology and parameters for calculating the doses due to the actual release rates of the subject materials are consistent with the methodology provided in Regulatory Guide 1.109, "Calculation of Annual Doses to Man from Routine Releases of Reactor Effluents for the Purpose of Evaluating Compliance with 10 CFR Part 50, Appendix I," Revision 1, October 1977 and Regulatory Guide 1.111, "Methods for Estimating Atmospheric Transport and Dispersion of Gaseous Effluents in Routine Releases from Light-Water-Cooled Reactors," Revision 1, July 1977.

These equations also provide for determining the actual doses based upon the historical average atmospheric conditions. The release rate controls for iodine-1 31, iodine-133, tritium, and radionuclides in particulate form with half lives greater than 8 days are dependent upon the existing radionuclide pathways to man, in the areas at and beyond the SITE BOUNDARY. The pathways that were examined in the development of these calculations were: (1) individual inhalation of airborne radionuclides, (2) deposition of radionuclides onto green leafy vegetation with subsequent consumption by man, (3) deposition onto grassy areas where milk animals and meat producing animals graze with consumption of the milk and meat by man, and (4) deposition on the ground with subsequent exposure of man.

3/4.11.2.4 OFF-GAS TREATMENT SYSTEM The FUNCTIONAL CAPABILITY of the OFF-GAS TREATMENT SYSTEM ensures that the system will be available for use whenever gaseous effluents require treatment prior to release to the environment. The requirement that the appropriate portions of these systems be used, when specified, provides reasonable assurance that the releases of radioactive materials in gaseous effluents will be kept "as low as is reasonably achievable." This control implements the requirements of General Design Criteria 60 of Appendix A to 10 CFR Part 50, and the design objectives given in Section II.D of Appendix I to 10 CFR Part 50. The specified limits governing the use of appropriate portions of the systems were specified as a suitable fraction of thedose design objectives set forth in Sections II.B and II.C of Appendix I, 10 CFR Part 50, for gaseous effluents.

FERMI 2 ODCM - TRM VOLUME II 4-5 Rev. 13

RADIOACTIVE EFFLUENTS BASES 3/4.11.2.5 VENTILATION EXHAUST TREATMENT SYSTEM The requirement that the appropriate portions of this system be used, when specified, provides reasonable assurance that the releases of radioactive materials in gaseous effluents will be kept "as low as is reasonably achievable." The specified limits governing the use of appropriate portions of the systems were specified as a suitable fraction of the dose design objectives set forth in Sections II.B and II.C of Appendix 1,10 CFR Part 50, for gaseous effluents.

3/4.11.2.8 VENTING OR PURGING This control provides reasonable assurance that releases from primary containment purging operations will not exceed the annual dose limits of 10 CFR Part 20 for UNRESTRICTED AREAS.

3/4.11.4 TOTAL DOSE This control is provided to meet the dose limitations of 40 CFR Part 190 that have been incorporated into 10 CFR Part 20 by 46 FR 18525. The control requires the preparation and submittal of a Special Report whenever the calculated doses from plant generated radioactive effluents and direct radiation exceed 25 mrem to the total body or any organ, except the thyroid, which shall be limited to less than or equal to 75 mrems. For sites containing up to 4 reactors, it is highly unlikely that the resultant dose to a member of the public will exceed the dose limits of 40 CFR Part 190 if the individual reactors remain within twice the dose design objectives of Appendix I, and if direct radiation doses from the reactor units and outside storage tanks are kept small. The Special Report will describe a course of action that should result in the limitation of the annual dose to a member of the public to within the 40 CFR Part 190 limits. For the purpose of the Special Report, it may be assumed that the dose commitment to the member of the public from other than uranium fuel cycle sources is negligible, with the exception that dose contributions from other nuclear fuel cycle facilities at the same site or within a radius of 8 km must be considered. If the dose to any member of the public is estimated to exceed therequirements of 40 CFR Part 190, the Special Report with a request for a variance (provided the release conditions resulting in violation of 40 CFR Part 190 have not already been corrected), in accordance with the provisions of 40 CFR Part 190.11 and 10 CFR Part 20.2203, is considered to be a timely request and fulfills the requirements of 40 CFR Part 190 until NRC staff action is completed. The variance only relates to the limits of 40 CFR Part 190, and does not apply in any way to the other requirements for dose limitation of 10 CFR Part 20, as addressed in Controls 3.11.1.1 and 3.11.2.1. An individual is not considered a member of the public during any period in which he/she is engaged in carrying out any operation that is part of the nuclear fuel cycle.

FERMI 2 ODCM - TRM VOLUME II 4-6 Rev. 13

RADIOLOGICAL ENVIRONMENTAL MONITORING BASES 3/4.12.1 MONITORING PROGRAM The radiological environmental monitoring program required by this control provides representative measurements of radiation and of radioactive materials in those exposure pathways and for those radionuclides that lead to the highest potential radiation exposures of MEMBERS OF THE PUBLIC resulting from the station operation. This monitoring program implementsSection IV.B.2 of Appendix I to 10 CFR Part 50 and thereby supplements the radiological effluent monitoring program by verifying that the measureable concentrations of radioactive materials and levels of radiation are not higher than expected on the basis of the effluent measurements and the modeling of the environmental exposure pathways. Guidance for this monitoring program is provided by the Radiological Assessment Branch Technical Position on Environmental Monitoring. The initially specified monitoring program will be effective for at least the first 3 years of commercial operation. Following this period, program changes may be initiated based on operational experience.

The required detection capabilities for environmental sample analyses are tabulated in terms of the lower limits of detection (LLDs). The LLDs required by Table 4.12.1-1 are considered optimum for routine environmental measurements in industrial laboratories. It should be recognized that the LLD is defined as an a priori (before the fact) limit representing the capability of a measurement system and not as an a posteriori (after the fact) limit for a particular measurement.

Detailed discussion of the LLD, and other detection limits, can be found in HASL Procedure Manual, HASL-300 (revised annually), Currie, L. A., "Limits for Qualitative Detection and Quantitative Determination - Application to Radiochemistry," Anal. Chem. 40, 586-93 (1968),

and Hartwell, J. K., "Detection Limits for Radioanalytical Counting Techniques," Atlantic Richfield Hanford Company Report ARH-SA-215 (June 1975).

3/4.12.2 LAND USE CENSUS This control is provided to ensure that changes in the use of areas at and beyond the SITE BOUNDARY are identified and that modifications to the radiological environmental monitoring program are made if required by the results of this census. The best information from the door-to-door survey, from aerial survey, from visual survey or from consulting with local agricultural authorities shall be used. This census satisfies the requirements of Section IV.B.3 of 2

Appendix I to 10 CFR Part 50. Restricting the census to gardens of greater than 50 m provides assurance that significant exposure pathways via leafy vegetables will be identified and monitored since a garden of this size is the minimum required to produce the quantity (26 kg/year) of leafy vegetables assumed in Regulatory Guide 1.109 for consumption by a child. To determine this minimum garden size, the following assumptions were made: (1) 20% of the garden was used for growing broad leaf vegetation (i.e., similar to lettuce and cabbage), and (2) a vegetation yield of 2 kg/m 2 .

FERMI 2 ODCM - TRM VOLUME II 4-7 Rev. 13

RADIOLOGICAL ENVIRONMENTAL MONITORING BASES 3/4.12.3 INTERLABORATORY COMPARISON PROGRAM The requirement for participation in an Interlaboratory Comparison Program which is audited periodically is provided to ensure that independent checks on the precision and accuracy of the measurements of radioactive material in environmental sample matrices are performed as part of the quality assurance program for environmental monitoring in order to demonstrate that the results are valid for the purposes of Section IV.B.2 of Appendix I to 10 CFR Part 50.

END OF SECTION 4.0 FERMI 2 ODCM - TRM VOLUME II 4-8 Rev. 13

(

SECTION 5.0 ADMINISTRATIVE CONTROLS FERMI 2 ODCM - TRM VOLUME II 5-1 Rev. 13

ADMINISTRATIVE CONTROLS ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT 5.9.1.7 Routine Annual Radiological Environmental Operating Reports covering the operation of the unit during the previous calendar year shall be submitted prior to May 1 of each year.

The initial report shall be submitted prior to May 1 of the year following initial criticality.

The Annual Radiological Environmental Operating Reports shall include summaries, interpretations, and an analysis of trends of the results of the radiological environmental surveillance activities for the report period, including a comparison as appropriate, with preoperational studies, with operational controls, and with previous environmental surveillance reports, and an assessment of the observed impacts of the plant operation on the environment.

The reports shall also include the results of land use censuses required by Control 3.12.2. The Annual Radiological Environmental Operating Reports shall include the results of analysis of all radiolog.ical environmental samples and of all environmental radiation measurements taken during the period pursuant to the locations specified in Table 10.0-1 in the ODCM, as well as summarized and tabulated results of these analyses and measurements in the format of the table in the Radiological Assessment Branch Technical Position, Revision 1, November 1979.

In the event that some individual results are not available for inclusion with the report, the report shall be submitted noting and explaining the reasons for the missing results. If possible, the missing data shall be submitted as soon as possible in a supplementary report.

The reports shall also include the following: a summary description of the radiological environmental monitoring program; one or more tables covering all sampling locations; the results of licensee participation in the Interlaboratory Comparison Program, required by Control 3.12.3; discussion of all deviations from the sampling schedule of Table 3.12.1 -1;- and discussion of all analyses in which the LLD required by Table 4.12.1-1 was not achievable.

ANNUAL RADIOACTIVE EFFLUENT RELEASE REPORT*

5.9.1 .8 Routine Annual Radioactive Effluent Release Reports covering the operation of the unit during the previous year of operation shall be submitted prior to May 1 of each year.. The period of the first report shall begin with the date of initial criticality.

A single submittal may be made for a mutiple unit station. The submittal should combine those sections that are common to all units at the station; however, for units with separate radwaste systems, the submittal shall specify the releases of radioactive material from each unit.

FERMI 2 ODCM - TRM VOLUME 1152Re.1 5-2 Rev. 13

ADMINISTRATIVE CONTROLS ANNUAL RADIOACTIVE EFFLUENT RELEASE REPORT (Continued)

The Annual Radioactive Effluent Release Report shall include a summary of the quantities of radioactive liquid and gaseous effluents and solid waste released from the unit as outlined in Regulatory Guide 1.21, "Measuring, Evaluating, and Reporting Radioactivity in Solid Wastes and Releases of Radioactive Materials in Liquid and Gaseous Effluents from Light-Water-Cooled Nuclear Power Plants," Revision 1, June 1974, with data summarized on a quarterly basis following the format of Appendix B thereof.

The Annual Radioactive Effluent Release Report shall include an annual summary of hourly meteorological data collected over the previous year. This annual summary may be either in the form of an hour-by-hour listing on an electronic medium of wind speed, wind direction, atmospheric stability, and precipitation (if measured), or in the form of joint frequency distributions of wind speed, wind direction, and atmospheric stabilityi*** This same report shall include an assessment of the radiation doses due to the radioactive liquid and gaseous effluents released from the unit or station during the previous calendar year. This same report shall also include an assessment of the radiation doses from radioactive liquid and gaseous effluents to MEMBERS OF THE PUBLIC due to their activities inside the SITE BOUNDARY (Figure 3.0-1) during the report period. All assumptions used in making these assessments, i.e., specific activity, exposure time and location, shall be included in these reports. The assessment of radiation doses shall be performed in accordance with the methodology and parameters in the OFFSITE DOSE CALCULATION MANUAL (ODCM).

The Annual Radioactive Effluent Release Report shall also include an assessment of radiation doses to the likely most exposed MEMBER OF THE PUBLIC from reactor releases and other nearby uranium fuel cycle sources, including doses from primary effluent pathways and direct radiation, for the previous calendar year to show conformance with 40 CFR Part 190, Environmental Radiation Protection Standards for Nuclear Power Operation. The assessment of radiation doses shall be performed in accordance with methodology and parameters in the ODCM.

The Annual Radioactive Efluent Release Reports shall include the following information for each class of solid waste (as defined by 10 CFR Part 61) shipped offsite during the report period:

a. Total volume in all containers,

b. Total curie quantity (specify whether determined by measurement or estimate),

- - In lieu of submission with the Annual Radioactive Effluent Release Report, the licensee has the option of retaining this summary of required meteorological data on site in a file that shall be provided to the NRC upon request.

FERMI 2 ODCM - TRM VOLUME II 5-3 Rev. 13

ADMINISTRATIVE CONTROLS ANNUAL RADIOACTIVE EFFLUENT RELEASE REPORT (Continued)

c. Principal radionuclides (specify whether determined by measurement or

-estimate),

d. Source of waste and processing employed (e.g., dewatered spent resin, compacted dry waste, evaporator bottoms),

e. Type of container (e.g., LSA, Type A, Type B, Large Quantity), and

f. Solidification agent or absorbent (e.g., cement, urea formaldehyde).

The Annual Radioactive Effluent Release Reports shall include a list and description of unplanned releases from the site to UNRESTRICTED AREAS of radioactive materials in gaseous and liquid effluents made during the reporting period.

The Annual Radioactive Effluent Release Reports shall include any changes made during the reporting period to the OFFSITE DOSE CALCULATION MANUAL (ODCM) as described in Technical Specification 5.5.1.3, as well as a listing of new locations for dose calculations and/or environmental monitoring identified by the land use census pursuant to Control 3.12.2.

The Annual Radioactive Effluent Release Reports shall also include the following: an explanation as to why the not FUNCTIONALLY CAPABLE status of liquid or gaseous effluent monitoring instrumentation was not corrected within the time specified in Control 3.3.7.11 or 3.3.7.12, respectively; and description of the events leading to liquid holdup tanks exceeding the limits of Technical Specification 5.5.8.6.

The Annual Radioactive Effluent Release Reports shall include the results of analysis of all onsite groundwater sampling and a description of any detected onsite radioactive leaks or spills 3 /01 into groundwater.

5.15 MAJOR CHANGES TO RADIOACTIVE LIQUID, GASEOUS, AND SOLID WASTE TREATMENT SYSTEMS*

5.15.1 Licensee-initiated major changes to the radioactive waste systems (liquid, gaseous, and solid):

a. Shall be reported to the Commission in the Annual Radioactive Effluent Release Report for the period in which the evaluation was reviewed by the OSRO. The discussion of each change shall contain:

1. A summary of the evaluation that led to the determination that the change could be made in accordance with 10 CFR 50.59.

2. Sufficient detailed information to totally support the reason for the change without benefit of additional or suppiementai information;

Licensees may choose to submit the information called for in this Control as part of the UFSAR TeS-irraccordance with- 10 -FR-50.7It(e).

Note: Page content was last changed with ODCM Revision 17.

5-4 Rev. 18 FERMI 2 0DCM - TRM VOLUME II

ADMINISTRATIVE CONTROLS

3. A detailed description of the equipment, components, and processes involved and the interfaces with other plant systems;

4. An evaluation of the change, which shows the predicted releases of radioactive materials in liquid and gaseous effluents and/or quantity of solid waste that differ from those previously predicted in the license application and amendments thereto;

5. An evaluation of the change, which shows the expected maximum exposures to a MEMBER OF THE PUBLIC in the UNRESTRICTED AREA and to the general population that differ from those previously estimated in the license application and amendments thereto;

6. A comparison of the predicted releases of radioactive materials, in liquid and gaseous effluents and in solid waste, to the actual releases for the period prior to when the changes are to be made;

7. An estimate of the exposure to plant operating personnel as a result of the change; and

8. Documentation of the fact that the change was reviewed and found acceptable by the OSRO.

b. Shall become effective upon review and acceptance by the OSRO.

END OF SECTION 5.0 FERMI 2 ODCM - TRM VOLUME 1155Re.1 5-5 Rev. 13

Nuclear Production - Fermi 2 ODCM-6.0 Offsite Dose Calculation Manual Page 6.0-1 PART II CALCULATIONAL METHODS

SECTION 6.0 LIQUID EFFLUENTS FERMI 2 ODCM - TRM VOLUME II 6-1 Rev. 13

6.0 LIQUID EFFLUENTS This section summarizes information on the liquid effluent radiation monitoring instrumentation and controls. More detailed information is provided in the Fermi 2 UFSAR and Fermi 2 design drawings from which this summary was derived. This section also describes the sampling and analysis required by the Offsite Dose Calculation Manual. Methods for calculating alarm setpoints for the liquid effluent monitors are presented. Also, methods for evaluating doses from liquid effluents are provided.

6.1 Radiation Monitoring Instrumentation and Controls This section summarizes the instrumentation and controls monitoring liquid effluents. This discussion focuses on the role of this equipment in assuring compliance with the Offsite Dose Calculation Manual.

6.1.1 Offsite Dose Calculation Manual (ODCM) 3.3.7.11 Requirement Fermi 2 ODCM 3.3.7.11 prescribes the monitoring required during liquid releases and the backup sampling required when monitors are not FUNCTIONALLY CAPABLE.

The liquid effluent monitoring instrumentation for controlling and monitoring radioactive effluents in accordance with the Fermi 2 ODCM 3.3.7.11 is summarized below:

1. Radiation Alarm - Automatic Release Termination

a. Liquid Radwaste Effluent Line - The D1 1-N007 Radiation Monitor on the liquid radwaste effluent line provides the alarm and automatic termination of liquid radioactive material releases prior to exceeding 1 Maximum Permissible Concentration (MPC) at the discharge to Lake Erie, as required by ODCM 3.3.7.11. The monitor is located upstream of the Isolation Valve (G 11-F733) on the liquid radwaste discharge line and monitors the concentration of liquid effluent before dilution by the circulating water reservoir (CWR) decant flow.

2. Radiation Alarm (only)

a. Circulating Water Reservoir (CWR) Decant Line - The CWR Decant Line Radiation Monitor (D1 1-N402) provides indication of the concentration of radioactive material in the diluted radioactive liquid releases just before discharge to Lake Erie. As required by ODCM 3.3.7.11, the alarm setpoint is established to alarm (only) prior to exceeding one MPC.

FERMI 2 0DCM - TRM VOLUME II 6-2 Rev. 13

3. Flow Rate Measuring Devices

a. Liquid Radwaste Effluent Line - In accordance with ODCM 3.3.7.11, the release rate of liquid'radwaste discharges is monitored by Gi 1-R703.

This flow rate instrumentation is located on the radwaste discharge line prior to the junction with the CWR decant line.

b. Circulating Water Reservoir Decant Line - The flow rate measuring device for the CWR decant line has been removed. The flow rate of the CWR decant line is now measured using certified pump performance curves for the CWR decant pumps, together with readings from pump discharge pressure gauges and reservoir level indication.

6.1.2 Non-ODCM Required Monitor An additional monitor not required by Fermi 2 0DCM is provided by Detroit Edison to reduce the likelihood of an unmonitored release of radioactive liquids.

1 General Service Water - The General Service Water (GSW) Radiation Monitor (D 11-N008) provides additional control of potential radioactive effluents. D1 1-N008 monitors the GSW System prior to discharge into the Main Condenser circulating water discharge line to the Circulating Water Reservoir. Although not an ODCM required monitor, D11 -N008 monitors a primary liquid stream in the plant that also discharges to the environment (Lake Erie via the Circulating Water Reservoir). Indication of radioactive material contamination in the GSW System would also indicate potential CWR contamination and the need to control all discharges from the CWR as radioactive effluents.

FERMI 2 ODCM - TRM VOLUME II 6-3 Rev. 14

6.2 Sampling and Analysis of Liquid Effluents The program for sampling and analysis of liquid waste is prescribed in the Fermi 2 Offsite Dose Calculation Manual Table 4.11.1.1.1-1. This table distinguishes two types of liquid releases: a) BATCH releases, defined as discrete volumes, from the Waste Sample Tanks (normally after processing through the radwaste system), and b) CONTINUOUS releases, from the Circulating Water Reservoir (CWR) System, if it becomes contaminated.

Continuous releases from the CWR System are via the CWR decant line to Lake Erie.

The CWR System is not expected to become contaminated. Therefore, continuous radioactive material releases are not expected. However, the General Service Water (GSW) and the CWR systems interface with radioactive systems in the plant. Also, the GSW intake is within a few hundred feet of the CWR decant line discharge to Lake Erie.

For these reasons, it is prudent to consider the GSW and the CWR a potential source of radioactive effluents and to sample them regularly.

6.2.1 BATCH Releases Fermi 2 ODCM Table 4.11.1.1.1-1 requires that a sample representative of the tank contents be obtained before it is released. The table specifies the following program:

- Prior to sampling, the tank is isolated. The tank level is determined and this value is converted to tank volume. A pump with a known recirculation flow rate is then activated to recirculate tank contents. The pump is allowed to run for at least the time required to recirculate the tank volume twice.

- Prior to each batch release, analysis for principal gamma emitters and dissolved and entrained gases (including all peaks identified by gamma spectroscopy)

- Once per month, analysis of a composite sample of all releases that month for tritium (H-3) and gross alpha activity. (The composite sample is required to be representative of the liquids released and sample quantities of the composite are to be proportional to the quantities of liquid discharged).

- Once per quarter, analysis of a composite sample of all releases that quarter for Strontium (Sr)-89, Sr-90, and Iron (Fe)-55.

FERMI 2 ODCM - TRM VOLUME II 6-4 Rev. 13

6.2.2 CONTINUOUS Releases Fermi 2 CiCM Table 4.11.1.1.11-1 requires that composite samples be collected from the CWR System, if contaminated. The table specifies the following sample analysis:

- Once per month, analysis of a composite sample for principal gamma emitters and for 1-131.

- Once per month, analysis of a composite sample for H-3 and gross alpha.

- Once per month, analysis of weekly grab samples (composited) for dissolved and entrained gases (gamma emitters).

- Once per quarter, analysis for Sr-89, -90 and Fe-55.

6.3 Liquid Effluent Monitor Setpoints Offsite Dose Calculation Manual 3.11.1.1 requires that the concentration of liquid radioactive effluents not exceed the unrestricted area MPC at the discharge point to Lake Erie. Dissolved or entrained noble gases in liquid effluents are limited to a concentration of 2 E-04 pCi/ml, total noble gas activity. ODCM 3.3.7.11 requires that radiation monitor setpoints be established to alarm prior to exceeding the limits of ODCM 3.11.1.1.

To meet this specification, the alarm setpoints for liquid effluent monitors are determined in accordance with the following equation:

S CL(DF + PR)

RR (6-1) where:

SP = the setpoint, in pCi/ml, of the monitor measuring the radioactivity concentration in the effluent line prior to dilution. The setpoint represents a value which, if exceeded, would result in concentrations exceeding the MPC in the unrestricted area CL = the effluent concentration limit (ODCM 3.11.1.1) corresponding to ten times the limits of 10 CFR Part 20.1302.b.2.i at the discharge point in pCi/ml, defined in Equation (6-4)

FERMI 2 ODCM - TRM VOLUME II 6-5 Rev. 13

RR = the liquid effluent release rate as measured at the radiation monitor location, in volume per unit time, but in the same units as DF, below DF = the dilution water flow as measured prior to the release point (Lake Erie) in volume per unit time At Fermi 2 the available Dilution Water Flow (DF) is essentially constant for a given release, and the waste tank Release Rate (RR) and monitor Setpoint (SP) are set to meet the condition of Equation (6-1) for a given effluent Concentration Limit, CL.

NOTE: If no dilution is provided, SP < CL. Also, when DF is large compared to RR, then (DF + RR)-DF, and DF may be used instead of (DF + RR) as a simplification, as in Equation (6-5).

6.3.1 Liquid Radwaste Effluent Line Monitor The Liquid Radwaste Effluent Line Monitor D 11-N007 provides alarm and automatic termination of releases prior to exceeding MPC. As required by 0DCM Table 4.11.1.1.1-1 and as discussed in ODCM Section 6.2.1, a sample of the liquid radwaste to be discharged is collected and analyzed by gamma spectroscopy to identify principal gamma emitting radionuclides. From the measured individual radionuclide concentrations, the allowable release rate is determined.

The allowable release rate is inversely proportional to the ratio of the radionuclide concentrations to the MPC values. The ratio of the measured concentration to MPC values is referred to as the "MPC fraction" and is calculated by the equation:

MPCF=ZMPC, C, (6-2) where:

MPCF = fraction of the unrestricted area MPC for a mixture of gamma emitting radionuclides Ci concentration of each gamma emitting radionuclide i measured in each tank prior to release (pCi/ml)

MPCi unrestricted area most restrictive MPC for each radionuclide i: ten times the value from 10 CFR Part 20, Appendix B, Table 2, Column 2. For dissolved and entrained noble gases an MPC value of 2E-04 pCi/ml may be used, but noble gases need not be included in this calculation.

FERMI 2 ODCM - TRM VOLUME II 6-6 Rev. 13

Including noble gases in Equation (6-2) eliminates the need for a separate evaluation of compliance with the noble gas concentration limit of ODCM 3.11.1.1.

Based on the MPCF, the maximum allowable release rate can be calculated by the following equation:

DF MAX RR!< (APCFV*(I + BF))+ H3MPCF

SF (6-3) where:

MAX RR = maximum acceptable waste tank discharge rate (gal/min)

(Monitor #G11-R703)

DF dilution flow rate from the CWR decant line, measured as described in 0DCM section 6.1.1.3.b.

SF administrative safety factor to account for variations in monitor response and flow rates. A SF value of 0.5 is suggested because it provides for 100% variation caused by statistical fluctuation and/or errors in measurements.

BF conservative estimate of the ratio of the MPC fraction of pure beta emitters other than tritium to the gamma MPC fraction (MPCF) (The value 0.10 may be used for BF.)

MPCF = As previously defined by equation (6-2)

H3MPCF = conservative estimate of MPC fraction due to tritium (The value 0.13 may be used for H3MPCF.)

NOTE: Equation (6-3) is valid only for MPCF >1; if the MPCF <1, the waste tank concentration meets the limits of 10 CFR Part 20 without dilution, and the tank may be discharged at the maximum rate.

If MAX RR as calculated above is greater than the maximum discharge pump capacity, the pump capacity should be used in establishing the actual Release Rate RR for the radwaste discharge. For a Waste Sample Tank, the maximum discharge rate is 50 gallons per minute. This Release Rate RR is monitored in the Radwaste Control Room by G 11-R703.

FERMI 2 ODCM - TRM VOLUME II 6-7 Rev. 14

The Concentration Limit (CL) of a liquid radwaste discharge, is the same as the effective MPC for the radionuclide mixture of the discharge. Simply, the CL (or effective MPC) represents the equivalent MPC value for a mixture of radionuclides evaluated collectively. The equation for determining CL is:

CL = 1C, MPCF (6-4)

Based on the Release Rate RR and Dilution Flow DF and by substituting Equation (6-4) for CL in Equation (6-1) and introducing sensitivity factors and factors to account for the presence of pure beta emitters, the alarm setpoint is calculated by the equation:

(C,* SEN,)* DF* H3F* SF+ Bkg MPCF* (I + BF)* RRI?

(6-5) where:

SP setpoint of the radiation monitor counts per second (cps) or counts per minute (cpm)

Ci concentration of radionuclide i as measured by gamma spectroscopy (pCi/ml)

SENi monitor sensitivity for radionuclide i based on calibration curve (cps/(pCi/ml) or cpm/(pCi/ml)) or single conservative value for all radionuclides (see below)

RR = actual release rate of the liquid radwaste discharge (gal/min)

BF = pure beta factor as defined for Equation (6-3)

MPCF = MPC fraction as determined by Equation (6-2)

H3F . correction factor to account for estimated tritium concentration at the discharge point (The value 0.99 may be used.)

Bkg = background reading of monitor (cps)

DF = dilution flow rate from the CWR decant line, measured as described in ODCM section 6.1.1.3.b. Also see note preceding Section 6.3.1.

SF 1 .0 when a single conservative sensitivity value is used; 0.5 when individual nuclide sensitivity factors are used FERMI 2 ODCM - TRM VOLUME !1 6-8 Rev. 14

The sensitivity of Cr-51 determined from the primary calibration sensitivity curves may be used as a single conservative value for SENi above. The Cr-51 sensitivity has been determined to be conservative based on the nuclide mixes which have been seen in actual liquid discharges from Fermi 2. For the D11-N007 monitor, a monitor sensitivity value of 1.0 E6 cps/(pCi/ml) may be used as the single conservative value of SENi.

If no radionuclides are measured by gamma spectroscopy, the alarm setpoint can be established at one half the setpoint of the most recent discharge for which radionuclides were detected by gamma spectroscopy.

Prior to conducting any batch liquid radwaste release, Equation (6-3) is used to determine the allowable release rate in accordance with ODCM 3.11 . 1.

Equation (6-5) is used to determine the alarm setpoint in accordance with ODCM 3.3.7.11.

6.3.2 Circulating Water Reservoir Decant Line Radiation Monitor (D1I-N402)

ODCM 3.3.7.11 requires that the setpoint for the CWR Decant Line Radiation Monitor D11 -N402 be established to ensure the radioactive material concentration in the decant line prior to discharge to Lake Erie does not exceed MPC, unrestricted area (ten times 10 CFR 20, Appendix B, Table 2, Column 2 values). The alproach for determining the alarm setpoint for the CWR Decant Line Radiation Monitor is the same as presented in Section 6.3.1. However, the CWR Decant Line Radiation Monitor setpoint need not be changed prior to each release. Equation (6-1) remains valid, except that, for the CWR Decant Line Monitor, the dilution flow previously assumed for diluting the BATCH liquid radwaste effluents is now the release rate. There is no additional dilution prior to discharge to Lake Erie. Thus, Equation (6-1) simplifies to:

SP < CL (6-6)

Substituting Equation (674) for CL. and introducing a safety factor, sensitivity factors, and monitor background, the D1 1-N402 alarm setpoint can be calculated by the equation:

SP Z(C,

SEN,)* SF MPCF (6-7)

FERMI 2 ODCM - TRM VOLUME II 6-9 Rev. 13

where:

SP = setpoint in counts per minute (cpm)

Ci = concentration of each radionuclide i in the CWR decant line effluent (pCi/ml)

SENi = monitor sensitivity for nuclide i based on calibration curve (cpm/(PCi/ml))

MPCF = MPC fraction as determined by Equation (6-2) with Ci defined as for Equation (6-7)

SF = 0.5, administrative safety factor Bkg = background reading of monitor (cpm)

Normally, only during periods of batch liquid radwaste discharges will there exist

,any plant-related radioactive material in the CWR decant line.

6.3.3 Generic, Conservative Alarm Setpoint for DII-N402 The D 11-N402 setpoint could be adjusted for each BATCH release as is done for the liquid radwaste effluent line monitor. Based on the measured levels of radioactive material in a BATCH liquid release, the alarm setpoint for D1 1-N402 could be calculated using Equation (6-7). However, during these planned releases, the concentrations will almost always be so low (due to dilution) that the D11-N402 Monitor will not indicate measurable levels. The CWR decant line design flow is 10,000 gpm; and the maximum liquid radwaste release rate is 50 gpm, providing a 200:1 dilution. The radioactive material concentration of BATCH liquid releases is typically in the range of 10-7 to 10-4 pCi/ml. With a nominal 200:1 dilution (actual dilution has been greater since in actual releases the decant line flow rate has been about 18,000 gpm), the CWR decant line monitor would monitor diluted activity in the range of 5 x 10-10 to 5 x 10-7 Ci/mI. D11-N402 Monitor response at these levels would be 0.1 to 100 cpm, depending on the particular radionuclide mixture and corresponding instrument response. These response levels are less than the monitor background levels.

In lieu of routinely adjusting the D1 1-N402 setpoints, generic, conservative setpoints have been established based on an analysis of nuclides seen in actual liquid discharges and on the primary calibration sensitivity curve.

FERMI 2 ODCM - TRM VOLUME II 6-10 Rev. 13

6.3.4 Alarm Setpoint for GSW and RHR System Radiation Monitors Levels of radioactive material detectable above background at Radiation Monitor D1 1-N008 would be one of the first indicators of contamination of the General Service Water (GSW) System and the CWR. Likewise, for the Residual Heat Removal (RHR) System, the D1 1-N401 A and B Monitors would be one of the first indicators of contamination and subsequent contamination of the CWR.

Therefore, to provide early indication and assure prompt attention, the alarm setpoints for these monitors should be established as close to background as possible without incurring a spurious alarm due to background fluctuations. This level is typically around three times background.

If the GSW System or RHR System becomes contaminated, it may become necessary to raise the radiation monitor setpoints. The alarm setpoints should be re-evaluated to provide the CR operator a timely indication of further increasing activity levels in the GSW or RHR System without spurious alarms.

The method for this re-evaluation is the same as described above - the alarm setpoint established at three times its current reading. No regulatory limits apply for establishing a maximum value for these alarm setpoints since these monitors are located on plant systems and do not monitor final release points to the environment. However, as a practical matter, upper limits on the alarm setpoints can be evaluated using the methods of ODCM Section 6.3.1 based on the actual system flows, dilution and release paths in effect at the time.

6.3.5 Alarm Response - Evaluating Actual Release Conditions Normally, liquid release rates are controlled and alarm setpoints are established to ensure that the release does not exceed the concentration limits of ODCM 3.11.1.1 at the discharge to Lake Erie. However, ifeither Monitor D11 -

N007 or D11 -N402 alarms during a liquid release, it becomes necessary to re-evaluate the release conditions to determine compliance with ODCM 3.11.1.1.

Following an alarm, the actual release conditions should be determined.

Radioactive material concentrations should be evaluated by sampling the effluent stream or resampling the waste tank. Discharge flow and dilution water flow should be redetermined.

To perform this evaluation, the following equation may be used for all nuclides, or dissolved and entrained noble gases may be evaluated separately from other nuclides using this equation:

___ RR ~(I +BF)1*

Mc, DF+RR H3F j (6-8)

FERMI 2 ODCM - TRM VOLUME II 6-11 Rev. 13

where:

Ci measured concentration of radionuclide i in the effluent stream (pCi/ml)

MPCi the MPC value for radionuclide i: ten times the 10 CFR 20, Appendix B, Table 2, Column 2 value (pCi/ml); 2 E-04 pCi/ml for dissolved or entrained noble gases RR actual release rate of the liquid effluent at the time of the alarm, gpm DF actual dilution circulating water flow at the time of the release alarm, gpm H3F,BF = as previously defined NOTE: For alarm on D1 1-N402 (CWR decant line), the Release Rate RR is the Dilution Water Flow DF and the DF term drops out of the equation.

6.3.6 Liquid Radwaste Monitor Setpoint Determination with Contaminated Circulating Water Reservoir In the event the CWR is determined to contain radioactive material, the effective dilution capacity of the CWR is reduced as a function of the MPCF. To determine the available dilution flow capacity the MPCF for the CWR is determined using equation (6-2). The MPCF of the CWR is used to determine the available dilution flow as follows:

CWR Dilution Flow = CWR Decant Flow Rate (GPM) * (1-CWR MPCF)

(6-9)

The resulting dilution flow rate is substituted in equation (6-3) to determine the maximum allowable release rate for discharges from the radwaste system.

Substituting the available CWR dilution flow from equation (6-9), the Liquid Radwaste Monitor maximum release rate can be determined using equation (6-3).

Once the available dilution flow and maximum allowable release rate have been determined the radwaste monitor setpoint can be determined using equation (6-5).

FERMI 2 ODCM - TRM VOLUME II 6-12 Rev. 13

6.4 Contaminated GSW or RHR System - Quantifying and Controlling Releases The GSW Radiation Monitor (D11 -N008) provides an indication of contamination of this system. The Monitors D11-N401 A and B perform this function for the RHR System.

Also, the CWR Decant Line Radiation Monitor monitors all liquid releases from the plant and would record any release to Lake Erie from either of these systems if contaminated.

As discussed in ODCM Section 6.2.2, sampling and analysis of the CWR System is required only if this system is contaminated, as would be indicated by D11-N402 or D11-N008. Nonetheless, periodic samples are collected from the CWR System to verify absence of contamination. Although not required by the ODCM, periodic sampling and analysis of the RHR System is also performed since it also is a potential source of contamination of the CWR and subsequent releases to Lake Erie. If contamination is found, further releases from the applicable system (GSW or RHR) via the CWR decant line must be evaluated and controlled to ensure that releases are maintained ALARA.

The following actions will be considered for controlling releases.

Sampling frequency of the applicable source (GSW or RHR System) and the CWR will be increased until the source of the contamination is found and controlled. This frequency may be relaxed after the source of contamination has been identified and isolated.

Gamma spectral analysis will be performed on each sample.

The measured radionuclide concentrations from the gamma spectral analysis will be compared with MPC (Equation 6-2) to ensure releases are within the limits of ODCM 3.11.1.1.

Based on the measured concentrations, the setpoint for the CWR Decant Line Radiation Monitor (D11-N402) will be determined as specified in Section 6.3.2. If the calculated setpoint based on the measured distribution is greater than the current setpoint (see ODCM Section 6.3.3) no adjustment to the setpoint is required.

Samples will be composited in accordance with ODCM Table 4.11.1.1.1-1 for monthly analysis for H-3 and gross alpha and for quarterly analysis for Sr-89, 90 and Fe-55.

Each sample will be considered representative of the releases that have occurred since the previous sample. For each sample (and corresponding release period), the volume of liquid released to the lake will be determined based on the measured CWR decant line cumulative flow.

From the sample analysis and the calculated volume released, the total radioactive material released will be determined and considered representative of the release penod. Cumulative doses Will be determined in accordance with ODCM Section 6.5.

FERMI 2 ODCM - TRM VOLUME II 6-13 Rev. 13

6.5 Liquid Effluent Dose Calculation - 10 CFR 50 The parameters of the liquid release (or estimated parameters, for a pre-release calculation) may be used to calculate the potential dose to the public from the release (or planned release). The dose calculation provides a conservative method for estimating the impact of radioactive effluents released by Fermi 2 and for comparing that impact against limits set by the NRC in the Fermi 2 ODCM. The limits in the Fermi 2 ODCM are specified as quarterly and calendar year limits. This assures that the average over the year is kept as low as reasonably achievable.

6.5.1 MEMBER OF THE PUBLIC Dose - Liquid Effluents ODCM 3.11.1.2 limits the dose or dose commitment to MEMBERS OF THE PUBLIC from radioactive materials in liquid effluents from Fermi 2 to:

- during any calendar quarter:

< 1.5 mrem to total body

< 5.0 mrem to any organ

- during any calendar year;

< 3.0 mrem to total body

< 10.0 mrem to any organ ODCM 4.11.1.2 requires that quarterly and annual cumulative dose due to liquid effluents be determined at least once per 31 days. The calculation of the potential doses to MEMBERS OF THE PUBLIC is a function of the radioactive material releases to the lake, the subsequent transport and dilution in the exposure pathways, and the resultant individual uptake. At Fermi 2, pre-operational evaluation of radiation exposure pathways indicated that doses from consumption of fish from Lake Erie provided the most conservative estimate of doses from releases of radioactive liquids. However, with the proximity of the water intakes for the City of Monroe and Frenchtown Township, it must be assumed that individuals will consume drinking water as well as fish that might contain radioactivity from discharges into Lake Erie.

Study of the currents in Lake Erie indicates that the current in the Lagoona Beach embayment carries liquid effluents from Fermi 2 north along the coast part of the time and south along the coast part of the time. When the current flows north, liquid effluents are carried away from the drinking water Intakes, so only the fish consumption exposure pathway must be considered.

When the current flows south, toward the drinking water Intakes, both fish consumption and drinking water consumption exposure pathways must be considered. To ensure conservatism in the dose modeling, the combined fish and drinking water pathway is used for evaluating the maximum. hypothetical dose to a MEMBER:OF THE PUBLIC from liquid radioactive effluents. The following calculational methods may be used for determining the dose or dose commitment due to the liquid radioactive effluents from Fermi 2:

FERMI 2 ODCM - TRM VOLUME II 6-14 Rev. 13

D, 1.67 E-0 2

VOL .(C

A)

DF* Z (6-10) where:

Do = dose or dose commitment to organ o or total body (mrem) due to release of a single tank Aio = site-specific ingestion dose commitment factor to the total body or any organ o for radionuclide i (mrem/hr per pCi/ml)

Ci = concentration of radionuclide i in undiluted liquid effluent representative of the volume VOL (pCi/ml)

VOL = total volume of liquid effluent released (gal)

DF = average dilution water flow (CWR decant line) during tank release (gal/min)

Z = 5, near field dilution factor (Derived from Regulatory Guide 1.109, Rev 0) 1.67 E-02 = 1 hr/60 min The site-specific ingestion dose/dose commitment factors (Aio) represents a composite dose factor for the fish and drinking water pathway. The site-specific dose factor is based on the NRC's generic maximum individual consumption rates. Values of Aio are presented in Table 6-1. They were derived in accordance with guidance of NUREG-0133 from the following equation:

, 1.14 E.+ 05 [(U,. i Dj,) + (U,..

BF)] DZ (6-11) where:

UF 21 kg/yr adult fish consumption UW 730 liters/yr adult water consumption DW 13.4, additional dilution from the near field to the water intake for Frenchtown Township (Net dilution factor of 67 from discharge point to a point documented in Fermi 2 UFSAR, Chapter 11, which is closer to the discharge point than this drinking water intake)

BFi = Bioaccumulation factor for radionuclide i in fish from Table 6.0-2 (pCi/kg per pCi/liter)

FERMI 2 ODCM - TRM VOLUME II 6-15 Rev. 13

DFi dose conversion factor for nuclide i for adults in organ o from Table E-11 of Regulatory Guide 1.109 (mrem/pCi) 6

103(mi / kg) 1.14 E + 05 = 10 (pCi/uCi) 8760 (hr / yr)

The radionuclides included in the periodic dose assessment required by ODCM 3.11.1.2 are those identified by gamma spectral analysis of the liquid waste samples collected and analyzed per the requirements of ODCM Table 4.11.1.1.1-1. In keeping with the NUREG-0133 guidance, the adult age group represents the maximum exposed individual age group. Evaluation of doses for other age groups is not required for demonstrating compliance with the dose criteria of ODCM 3.11.1.2. The dose analysis for radionuclides requiring radiochemical analysis will be performed after receipt of results of the analysis of the composite samples. In keeping with the required analytical frequencies of ODCM Table 4.11.1.1.1-1, tritium dose analyses will be performed at least monthly; Sr-89, Sr-90 and Fe-55 dose analyses will be performed at least quarterly.

6.5.2 Contaminated CWR System - Dose Calculation If the CWR System becomes contaminated, releases via the CWR System to Lake Erie must be included in the evaluation of the cumulative dose to a MEMBER OF THE PUBLIC as required by ODCM 3.11.1.2. ODCM Section 6.4 described the methods for quantifying and controlling releases from the CWR System.

For calculating the dose to a MEMBER OF THE PUBLIC, Equation (6-10) remains applicable for releases from the GSW System with the following assumptions:

- DF, Dilution Flow, is set equal to the average CWR decant line flow rate over the release period.

- Ci, Radionuclide Concentration, is determined as specified in ODCM Section 6.4.

- VOL, Volume Released, is set equal to the total volume of the discharges to Lake Erie via the CWR decant line as specified in Section 6.4.

FERMI 2 ODCM - TRM VOLUME II 6-16 Rev. 13

6.6 Liquid Effluent Dose Projections 10 CFR 50.36a requires licensees to maintain and operate the Radwaste System to ensure releases are maintained ALARA. This requirement is implemented through ODCM 3.11.1.3. This section requires that the Liquid Radioactive Waste Processing System be used to reduce the radioactive material levels in the liquid waste prior to release when the projected dose in any 31 day period would exceed:

0.06 mrem to the total body, or 0.2 mrem to any organ When the projected doses exceed either of the above limits, the waste must be processed by the Liquid Radwaste System prior to release. This dose criteria for processing is established at one forty eighth of the design objective rate (3 mrem/yr, total body or 10 mrem/yr any organ) in any 31 day period.

The applicable Liquid Waste Processing System for maintaining radioactive material releases ALARA is the Mixed Bed Demineralizers as delineated in Figure 6-1. Alternately, the Waste Evaporator (presented in the Fermi 2 UFSAR, Section 11.2) can be used to meet the NRC ALARA design requirements. It may be used in conjunction with or in lieu of the Mixed Bed Demineralizers to meet the waste processing requirements of ODCM 3.11.1.3.

Each BATCH release of liquid radwaste is evaluated to ensure that cumulative doses are maintained ALARA. In keeping with the requirements of ODCM 3.11.1.3, dose projections are made at least once per 31 days to evaluate the need for additional radwaste processing to ensure future releases are maintained ALARA.

The following equations may be used for the dose projection calculation:

D,h, = D,(31 / d)

(6-14)

Dmap = Dma(31 / a)

(6-15) where:

Dtbp = the total body dose projection for the next 31 day period (mrem)

NOTE: The reference calendar quarter is normally the current calendar quarter. If there have been liquid releases in the previous quarter but not in the current quarter, the previous quarter should be used as the reference calendar quarter.

Dtb the cumulative total body dose for all releases to date in the reference calendar quarter (normally the current quarter) as determined by equation (6-10) or (6-12) (mrem)

FERMI 2 ODCM - TRM VOLUME II 6-17 Rev. 13

Dmaxp the maximum organ dose projection for the next 31 day period (mrem)

Dmax the cumulative maximum organ dose for all releases to date in the reference calendar quarter as determined by Equation (6-10) or (6-13) (mrem) d the number of days from the beginning of the reference calendar quarter to the date of the dose projection evaluation.

31 the number of days in projection FERMI 2 ODCM - TRM VOLUME II 6-18 Rev. 13

TABLE 6.0-1 Fermi 2 Site Specific Liquid Ingestion Dose Commitment Factors Aio (mrem/hr per uCilml)

Nuclide Bone Liver T Body Thyroid Kidney Lung GI-LLI H-3 8.78E-1 8.78E-1 8.78E-1 8.78E-1 8.78E-1 8.78E-1 C-14 3.13E+4 6.26E+3 6.26E+3 6.26E+3 6.26E+3 6.26E+3 6.26E+3 Na-24 4.18E+2 4.18E+2 4.18E+2 4.18E+2 4.18E+2 4.18E+2 4.18E+2 P-32 1.39E+6 8.63E+4 5.36E+4 - 1.56E+5 Cr-51 1.29E+O 7.70E-1 2.84E-1 1.71E+O 3.24E+2 Mn-54 4.40E+3 8.40E+2 1.31 E+3 - 1.35E+4 Mn-56 1.11E+2 1.97E+1 1.41E+2 3.54E+3 Fe-55 6.75E+2 4.67E+2 1.09E+2 - 2.60E+2 2.68E+2 Fe-59 1.07E+3 2.51E+3 9.60E+2 7.O0E+2 8.35E+3 Co-57 2.20E+1 3.66E+1 - - 5.59E+2 Co-58 9.38E1+1 2.10E+2 - - - 1.90E+3 Co-60 2.69E+2 5.94E+2 - - - 5.06E+3 Ni-63 3.19E+4 2.21E+3 1.07E+3 - - - 4.62E+2 Ni-65 1.30E+2 1.68E+1 7.69E+O - - - 4.27E+2 Cu-64 1.05E+1 4.92E+0 - 2.64E+1 - 8,94E+2 Zn-65 2.32E+4 7.38E+4 3.34E+4 - 4.94E+4 - 4.65E+4 Zn-69 4.94E+1 9.44E+1 6.57E+O - 6.14E+1 - 1.42E+1 Br-82 - 2.28E+3 - 2.62E+3

"-83 - 4.07E+1 - - 5.86E+t 84 - 5.27E+! - - 4.14E-4 Br-85 - 2.17E+O - - 1.01E-15 Rb-86 1.01E+5 4.71E+4 - - 1.99E+4 Rb-88 2.90E+2 1.54E+2 - - 4.01E-9 Rb-89 1.92E+2 1.35E+2 - - 1.12E-11 Sr-89 240E+4 - 6.90E+2 - - 3.85E+3 Sr-90 5.91E+5 - 1.45E+5 - 1.71E+4 Sr-91 4.42E+2 - 1.79E+1 - - 2.11E+3 Sr-92 1.68E+2 - 7.26E+O - - 3.32E+3 Y-90 6.36E-1 - 1.70E-2 - - - 6.74E+3 Y-91 m 6.OOE-3 - 2.33E-4 - - - 1.76E-2 Y-91 9.31E+O - 2.49E-1 - - 5.13E+3 Y-92 5.58E-2 - 1.63E-3 - - 9,78E+2 Y-93 1.77E-1 - 4.89E-3 - - 5.62E+3 Zr-95 4.29E-1 1.38E-1 9.31 E-2 2.16E-1 - 5,50E+2 Zr-97 2.37E-2 4.78E-3 2.19E-3 7.22E-3 - 148E+3 Nb-95 4.47E+2 2.49E+2 1.34E+2 2.46E+2 - 1.51 E+6 Nb-97 3.75E+O 9.48E-1 3.46E-1 1.11E+O - 3.50E+3 Mo-99 1.30E+2 2.47E+1 2.94E+2 - 3.01E+2

.Tc-99m 1.04E-2 2.94E-2 3.74E-1 4.46E71 1.44E-2 1.74E+1 Tc-10i 1I07E-2 1.54iE-2 1.51 E-1 2.78E-1 7.88E-3 4.63E-14

.. -RMI 2 ODCM - TRM VOLUME I6 6-19 Rev. 13

TABLE 6.0-1 Fermi 2 Site Specific Liquid Ingestion Dose Commitment Factors Aio (mremlhr per uCi/ml)

Nuclide Bone Liver T Body Thyroid Kidney Lung GI-LLI Ru-103 5.58E+0 2.40E+0 2.13E+1 6.51E+2 Ru-105 4.64E-1 - 1.83E-1 - 6.OOE+0 2.84E+2 Ru-106 8.29E+1 - 1.05E+1 1.60E+2 5.37E+3 Rh-103m - -

Rh-106 Ag-110rn 1,87E+0 1.73E+O 1.03E+0 - 341E+O 7.08E+2 Sb-124 2,41E+1 4.56E-1 9.56E+O 5.84E-2 - 1.88E+1 6,84E+2 Sb-125 1.54E+1 1.72E-1 3.66E+0 1.57E-2 1.19E+1 1.70E+2 Te-125m 2.58E+,3 9.36E+2 3.46E+2 7.77E+2 1.05E+4 - 1.03E+4 Te-127m 6.52E+3 2.33E+3 7.95E+2 1.67E+3 2.65E+4 - 2.19E+4 Te-127 1.06E+2 3.81E+1 2.29E+1 7.86E+1 4.32E+2 - 8.37E+3 Te-129m 1.11E+4 4.13E+3 1.75E+3 3.81EE+3 4.63E+4 - 5.58E+4 Te-129 3.03E+1 1.14E+1 7.37E+O 2.32E+1 1.27E+2 - 2.28E+1 Te-131m 1.67E+3 8.15E+2 6.79E+2 1.29E+3 8.26E+3 - 8.1OE+4 Te-131 1.90E÷1 7.93E+O 5.99E+O 1.56E+1 8.32E+1 - 2.69E+O Te-132 2.43E+3 1.57E+3 1.47E+3 1.73E+3 1.51E+4 - 7.43E+4 1-130 3.18E+1 9.39E+1 3.71E+1 7.96E+3 1.47E+2 - 8.09E+1

'31 1.75E+2 2.51 E+2 1.44E+2 8.21 E+4 4.30E+2 - 6.61E+I 2 8.55E+O 229E+1 8.00E+0 8.OOE+2 3.64E+1 - 4.30E+O

, ,33 5.98E+1 1.04E+2 3.17E+1 1.53E+4 1.82E+2 - 9.35E+1 1-134 4.46E+O 1.21E+1 4.34E+O 2.1OE+2 1.93E+1 - 1.06E-2 1-135 1.87E+1 4.89E+1 1.81E+1 3,22E+3 7.83E+1 - 5.52E+1 Cs-134 2.98E+5 7.10E+5 5.80E+5 2.30E+5 7.62E+4 1.24E+4 Cs-136 3.12E+4 1.23E+5 8.87E+4 6.86E+4 9.40E+3 1.40E+4 Cs-137 3.82E+5 5.23E+5 3.42E+5 1.77E+5 5Y90E+4 1.01 E+4 Cs-138 2.65E+2 5.23E+2 2.59E+2 3.84E+2 3,79E+1 2.23E-3 Ba-139 1.53E+0 1.09E-3 4.48E-2 1.02E-3 6.19E-4 2.72E+0 Ba-140 3.20E+2 4.03E-1 2.10E+1 1.37E-1 2.30E-1 6.60E+2 Ba-141 7.44E-1 5.62E-4 2.51 E-2 5.23E-4 3.19E-4 350E-10 Ba-142 3.36E-1 3.46E-4 2.12E-2 2.92E-4 1.96E-4 4.74E-19 La-140 1.65E-1 8.32E-2 2.23E-2 6.11E+3 La-142 8-46E-3 3.84E-3 9.58E-4 *-- 2.81E-+l1 Ce-141 8.05E-2 5.45E-2 6.18E-3 253E-2 - 2.08E+2 Ce-143 1-42E-2 1.05E+1 1.16E-3 - 4.62E-3 - 3.92E+2 Ce-144 4.20E+O 1.76E+O 2.25E-1 - 1.04E-0 - 1.42E+3 Pr-143 6.08E-1 244E-1 3.01E-2 -1.41E-1 - 2.66E+3 Pr-144 1.99E-3 8.26E-4 1,01E-4 - 4.66E-4 - 2.86E-10 Nd-147 4.16E-1 4.80E-1 287E-2 - 2.81E-1 - 2.3tE+3 W-187 2.97E+2 2.48E+2 8.67E+ !-8.12E+4 Np-239 3.59E-2 3.53E-3 1.94E-3 1.1OE-2 7.24E+2

.. MI 2 ODCM - TRM VOLUME II 6-20 Rev. 13

TABLE 6.0-2 Bioaccumulation Factors (BFi)

(pCi/kg per pCilliter)*

Element Freshwater Fish H 9.QE-01 C 4.6E+03 Na 1.OE+02 P 3.OE+03 Cr 2.OE+02 Mn 4.0E+02 Fe 1.OE+02 Co 5.OE+01 Ni 1.OE+02 Cu 5.OE+01 Zn 2.0E+03 Br 4.2E+02 Rb 2.OE+03 Sr 3.OE+01 Y 2.5E+01 Zr 3.3E+00 Nb 3.OE+04 Mo 1.0E+01 Tc 1.5E+01 Ru 1.OE+01 Rh 1.OE+01 Ag 2.3E+00 Sb 1.OE+00 Te 4.OE+02 I 1.5E+01 Cs 2.OE+03 Ba 4.OE+00 La 2.5E+01 Ce 1.OE+00 Pr 2.5E+01 Nd 2.5E+01 W 1.2E+03 Np 1.OE+01

Values in this table are taken from Regulatory Guide 1.109 except for phosphorus, which is adapted from NUREG/CR-1 336, and silver and antimony, which are taken from UCRL 50564, Rev 1, October 1972.

FERMI 2 0DCM - TRM VOLUME II 6-21 Rev. 13

FIGURE 6.0-1 Liquid Radioactive Effluent Monitoring and Processing Diagram T.

L.- ,Ri.

FERMI 2 0DCM - TRM VOLUME II 6-22 Rev. 13 1 END OF SECTION 6.0

SECTION 7.0 GASEOUS EFFLUENTS FERMI 2 ODCM - TRM VOLUME II 7-1 Rev. 13

7.0 GASEOUS EFFLUENTS 7.1 Radiation Monitoring Instrumentation and Controls 7.1.1 Effluent Monitoring - Ventilation System Releases The gaseous effluent monitoring instrumentation required at Fermi 2 for controlling and monitoring radioactive effluents are specified in ODCM 3.3.7.12.

The monitoring of each identified gaseous effluent release point must include the following:

- Noble Gas Activity Monitor

- Iodine Sampler (sample cartridge containing charcoal or silver zeolite)

- Particulate Sampler (filter paper)

- Sampler Flow Rate Monitor Meeting these requirements, a total of six Eberline SPING Monitoring Systems 5FC3 ihftýtll~d 6h thiý fiVýý g5ýeiU* Fle-kýe p~ii~tS (Onsite Storage Fac.ility, Radwaste Building, Turbine Building, Reactor Building Exhaust Plenum, and Standby Gas Treatment System Division 1 and Division 2). The SPING Monitor outputs are recorded electronically in the SS-1 Control Terminal in the Main Control Room.

In general, a reading exceeding the High alarm setpoint of the SPING Monitors causes an alarm in the Control Room. Fermi 2 ODCM Table 3.3.7.12-1 identifies these alarm functions.

7.1.2 Main Condenser Offgas Monitoring ODCM Table 3.3.7.12-1 and Technical Requirements Manual Volume 1, section TR 3.3.12, specify monitoring requirements for the Offgas System at the 2.2 minute delay line. The following monitors are required:

- Hydrogen Monitor - used to ensure the hydrogen concentration in.the Offgas Treatment System is maintained less than 4% by volume as required by Technical Requirements Manual Volume 1, section TRLCO 3.3.12.

Noble Gas Activity Monitor - used to ensure the gross activity release rate is maintained within 340 millicuries per second after 30 minute decay as required by Technical Specification 3.7.5.

These two monitors perform safety functions. The Hydrogen Monitor monitors the potential explosive mixtures in the Offgas System. The Noble Gas Monitor monitors the release rate from the main condenser ensuring doses at the exclusion area boundary will not exceed a smaii fraction of the limits of 10 CFR 100 in the event this effluent is inadvertently discharged directly to the environment bypassing the Offgas Treatment System.

Note: Page content was last changed with ODCM Revision 16.

FERMI 2 ODCM - TRM VOLUME il 7-2 Rev. 18

7.1.3 Reactor Building Ventilation Monitors (Gulf Atomic)

The Gulf Atomic Monitors (D11-N408 and 410) on the Reactor Building Ventilation System provide on high radiation levels (above alarm setpoint) initiation of SGTS, isolation of drywell vent/purge, isolation of the RB and Control Center Ventilation Systems and initiation of Control Center recirculation mode ventilation. These monitors and functions are not required by Fermi 2 0DCM but are important in controlling containment venting/purging.

7.2 Sampling and Analysis of Gaseous Effluents The program for sampling and analysis of gaseous waste is prescribed in Fermi 2 ODCM Table 4.11.2.1.2-1. This table distinguishes two types of gaseous releases:

(1) containment PURGE, treated as BATCH releases, and (2) discharges from the Reactor Building Exhaust Plenum (including Standby Gas Treatment System (SGTS) when operating), and other building ventilation exhausts, treated as CONTINUOUS releases.

7.2.1 Containment PURGE ODCM Table 4.11.2.1.2-1 requires that samples be collected and analyzed before each primary containment PURGE. Sampling and analysis is required within eight hours before starting a PURGE. ODCM Table 4.11.2.1.2-1 Footnote j and ODCM 4.11.2.8.2 also require that ifthe purging or venting is through the Reactor Building ventilation, rather than through SGTS, and if the primary containment radiation monitoring system is not FUNCTIONALLY CAPABLE or in alarm condition, sampling and analysis is required within 8 hours9.259259e-5 days 0.00222 hours 1.322751e-5 weeks 3.044e-6 months prior to and at least once per 12 hours1.388889e-4 days 0.00333 hours 1.984127e-5 weeks 4.566e-6 months during venting or purging of the primary containment. The required analyses must include principal gamma emitters and, if a pre-vent or pre-purge sample, tritium.

For a planned containment PURGE, the results of the samples and analyses may be used to establish the acceptable release rate and radiation monitor alarm setpoint in accordance with ODCM Sections 7.3 and 7.4. This evaluation may be necessary to ensure compliance with the dose rate limits of ODCM 3.11.2.1.

In practice, release flow rates are fairly constant and these calculations are necessary only if a threshold value of nuclide concentration in the primary containment atmosphere is reached. The alarm setpoints of the primary containment atmosphere monitor, the Reactor Building ventilation exhaust monitors, and the Reactor Building and SGTS SPING monitors are set to ensure that release routes are continuously monitored and controlled in accordance with 10 CFR 20 or limits specified in the ODCM.

FERMI 2 ODCM - TRM VOLUME II 7-3 Rev. 13

7.2.2 Ventilation System Releases ODCM Table 4.11.2.1.2-1 requires continuous samples of releases from the RB Exhaust Plenum, Standby Gas Treatment System, Radwaste Building, Turbine Building, and Onsite Storage Facility. The table specifies the following program:

- Once per week, analysis of an adsorbent sample of 1-131 and 1-133, plus analysis of a particulate sample for principal gamma emitters.

- Once per month, analysis of a composite particulate sample of all releases (by release point) that month for gross alpha activity.

- Once per quarter, analysis of a composite particulate sample of all releases that quarter for Sr-89 and Sr-90.

- Once per month, analysis of a grab' sample for principal gamma emitters (noble gases and tritium).

- Analysis of a grab sample for principal gamma emitters (noble gases) from the Offgas Vent Pipe sample lines, as needed to supplement RB Exhaust Plenum sampling. Normally performed monthly in conjunction with RB Exhaust Plenum grab sampling.

ODCM Table 4.11.2.1.2-1 also requires continuous monitoring for noble gases.

This requirement is met by the SPING Monitors on each of the plant gaseous release points.

The ODCM requires more frequent sampling and analysis following reactor startup, shutdown, or change in thermal power exceeding 15% within one hour.

The ODCM allows an exception to this increased sampling schedule when the applicable SPING noble gas monitor has not increased more than a factor of three.

Grab samples of the Fuel Pool Ventilation Exhaust are required tritium analysis once per seven days whenever spent fuel is in the Spent Fuel Pool. Also, grab samples for tritium are required when either the reactor well or the dryer separator pool is filled. These samples are taken at the Reactor Building Exhaust Plenum and Standby Gas Treatment System (SGTS) when operating.

FERMI 2 ODCM - TRM VOLUME iR 7-4 Rev. 18

7.3 Gaseous Effluent Monitor Setpoint Determination 7 3.1 Ventilation System Monitors Per the requirements of ODCM 3.3.7.12, alarm setpoints shall be established for the gaseous effluent monitoring instrumentation to ensure that the release rate of noble gases does not exceed the limits of ODCM 3.11.2.1. This section limits releases to a dose rate at the SITE BOUNDARY of 500 mrem/year to the total body or 3000 mrem/year to the skin. From a grab sample analysis of the applicable release (i.e., grab sample of the primary containment or Ventilation System release), the radiation monitoring alarm setpoints may be established by the following calculational method. The measured radionuclide concentrations and release rate are used to calculate the fraction of the allowable release rate, limited by ODCM 3.11.2.1, by the equation:

FRAC= 1.67E +01 z Q* VF* Z--(C,

K) 500 (7-1) 1.67E +01 * /Q* VF* (C, *[Li + 1.1M,)

FRAC=

3000 (7-2)

Where:

FRAC fraction of the allowable release rate based on the identified radionuclide concentrations and the release flow rate

%/Q = annual average meteorological dispersion to the controlling site boundary location from Table 7.0-3 (sec/m3 ) or plant procedures VF = Ventilation System flow rate for the applicable release point and monitor (liters/minute)

Ci = concentration of noble gas radionuclide i at release point as determined by gamma spectral analysis of grab sample (pCi/cc).

Ki = total body dose conversion factor for noble gas radionuclide i (mrem/yr per pCi/m 3, from Table 7.0-2)

Li = beta skin dose conversion factor for noble gas radionuclide i (mrem/yr per pCi/m 3, from Table 7.0-2)

FERMI 2 ODCM - TRM VOLUME II 7-5 Rev. 13

( Mi= gamma air dose conversion factor for noble gas radionuclide i (mrad/yr per pCi/m3 , from Table 7.0-2) 1.1 = mrem skin dose per mrad gamma air dose (mrem/mrad) 500 = total body dose rate limit (mrem/yr) 3000 = skin dose rate limit (mrem/yr) 1.67 E + 01 = 1 E + 03 (cc/liter) * (1/60) (min/sec)

Based on the more limiting (i.e., higher) value of FRAC as determined above, the alarm setpoints for the applicable monitors may be calculated by the equation:

s:

Sp<_ (AF* I c)++Bk g FRAC (7-3)

Where:

SP alarm setpoint corresponding to the maximum allowable release rate (pCi/cc)

Bkg background of the monitor (pCi/cc)

AF administrative allocation factor (Table 7.0-1) for the specific monitor and type release, which corresponds to the fraction of the total allowable release rate that is administratively allocated to the individual release points.

Ci concentration of Noble Gas Radionuclide i as determined by gamma spectral analysis of grab sample (pCi/cc). Note: If the monitor channel in question was showing a response to the effluent at the time of the grab sample, this response minus background may be used in lieu of the summed grab sample concentrations.

FERMI 2 ODCM - TRM VOLUME II 7-6 Rev. 13

The Allocation Factor (AF) is an administrative control imposed to ensure that combined releases from all release points at Fermi 2 will not exceed the regulatory limits on release rate from the site (i.e., the release rate limits of ODCM 3.11.2.1). From the Fermi 2 design evaluation of gaseous effluents presented in the UFSAR Section 11.3, representative values have been determined for AF. These values are presented in Table 7.0-1. These values may be changed in the future as warranted by operational experience, provided the site releases comply with ODCM 3.11.2.1. In addition to the allocation factor, safety factors which have the effect of lowering the calculated setpoints may be applied. When determining the Noble Gas Monitor calibration constant, the monitor sensitivity for Xe-133 may be used in lieu of the sensitivity values for the individual radionuclides. Because of its lower gamma energy and corresponding monitor response, the Xe-133 sensitivity provides a conservative value for alarm setpoint determination. Alternatively, if the monitor channel in question frequently shows a response to a mix of isotopes whose concentrations can be determined, the calibration constant may be determined from this type of data without reference to primary calibration data.

7.3.2 Setpoint Determination with No Nuclides Detected When noble gas concentrations for a release point cannot be determined from grab samples, there are two options for setpoint determination. First, the setpoint may be set slightly above monitor background (e.g. 2 to 3 times background). This approach may be used when releases are not expected from a particular release point. Second, the equations of Section 7.3.1 may be used with noble gas concentration values based either on UFSAR tables or on values from a release point for which concentrations have been determined (e.g. reactor building exhaust plenum). When this method is used, a safety factor should be used in the setpoint calculation.

7.3.3 Gaseous Effluent Alarm Response - Evaluating Actual Release Conditions The monitor alarm setpoint is used as the primary method for ensuring and demonstrating compliance with the release rate limits of ODCM 3.11 .2.1. Not exceeding alarm setpoints constitutes a demonstration that release rates have been maintained within the ODCM limits. When an effluent Noble Gas Monitor exceeds the alarm setpoint, an evaluation of compliance with the release rate limits must be performed using actual release conditions. This evaluation requires collecting a sample of the effluent to establish actual radionuclide concentrations and permit evaluating the monitor response. The following equations may be used for evaluating compliance with the release rate limit of ODCM 3.11.2.1 a:

D,ý, = 1.67E + 01

z / Q* VF* "(K

C,)

(7-4)

=1.67E +01* X/ Q* VF* -([L, +1.II* C,)

(7-5)

FERMI 2 ODCM - TRM VOLUME II 7-7 Rev. 13

Where:

Dtb = total body dose rate (mrem/yr)

DS= skin dose rate (mrem/yr)

X/ Q = atmospheric dispersion to the controlling SITE BOUNDARY location (sec/m3 )

VF Ventilation System release rate (liters/min)

Ci concentration of radionuclide i as measured in the grab sample or as correlated from the SPING Noble Gas Monitor reading (pCi/cc)

Ki total body dose conversion factor for noble gas radionuclide i (mrem/yr per pCi/m 3 , from Table 7.0-2)

Li beta skin dose conversion factor for noble gas radionuclide i (mrem/yr per pCi/m 3 , from Table 7.0-2)

Mi gamma air dose conversion factor for noble gas radionuclide i (mrad/yr per pCi/m 3 , from Table 7.0-2) 1.1 mrem skin dose per mrad gamma air dose (mrem/mrad) 1.67 E + 01 = 1 E + 03 (cc/liter) * (1/60) (min/sec)

The above equations may also be used to verify compliance with ODCM 3.11.2.1.a when noble gases are detected in periodic (e.g. monthly) effluent noble gas samples.

7.4 Primary Containment VENTING and PURGING 7.4.1 Release Rate Evaluation For primary containment VENTING or PURGING, an evaluation of acceptable release rate may be performed prior to the release. Based on the measured noble gas concentration in the grab sample collected per the requirements of ODCM Table 4.11.2.1.2-1, the allowable release rate from primary containment can be calculated by the following equation:

FERMI 2 ODCM - TRM VOLUME II 7-8 Rev. 13

RR,,, = 500 *AF 1.67 +O*z/ Q* (K *C)

(7-6) or 3000

AF 1.67E+Ol*x!/Q*X ([L,+1.IM,]*C,)

(7-7)

Where:

RRtb = allowable release rate so as not to exceed a dose rate of 500 mrem/yr, total body (liters/minute)

RRs = allowable release rate so as not to exceed a dose rate of 3000 mrem/yr, skin (liters/minute)

AF = allocation factor for the applicable release point from Table 7.0-1 (default value is 0.5 for Reactor Building Exhaust Plenum) 500 = total body dose rate limit (mrem/yr) 3000 = skin dose rate limit (mrem/yr)

The lesser value (RRtb or RRs) as calculated above may be used for establishing the allowable release rate for primary containment PURGING or VENTING, taking into account the fraction of the allocated release limit already accounted for by continuous releases from the proposed release point. As discussed in section 7.2.1, this evaluation is rarely necessary.

7.4.2 Alarm Setpoint Evaluation For a primary containment VENTING or PURGING, a re-evaluation of the alarm setpoint may be needed to ensure compliance with the requirements of ODCM 3.3.7.12. For the identified release path (RB Exhaust Plenum or SGTS) and associated effluent Radiation Monitor, the alarm setpoint should be calculated using Equations (7-1), (7-2) and (7-3). In Equations (7-1) and (7-2),

the value of the Ventilation Flow VF should be established at the total release flow rate, including the contribution from the PURGE or VENT. If the calculated alarm setpoint is greater than the current setpoint, no adjustments are necessary. As discussed in section 7.2.1, this setpoint evaluation is rarely necessary.

FERMI 2 ODCM - TRM VOLUME II 7-9 Rev. 13

7.5 Quantifying Releases - Noble Gases The determination of doses in the environment from releases is dependent on the mixture of the radioactive material. Also, NRC Regulatory Guide 1.21 requires reporting of individual radionuclides released in gaseous effluents. Therefore, Detroit Edison must determine the quantities of the individual radionuclides released. For noble gases, these quantities must be based on actual noble gas grab samples.

7.5.1 Sampling Protocol As required by ODCM 3.11.2.1, a gas sample is collected at least monthly from each of the five gaseous release points (Reactor Building Exhaust Plenum, Standby Gas Treatment System, Radwaste Building, Turbine Building, and Onsite Storage Facility). As discussed in ODCM Section 7.2.2, this gas sample is analyzed by gamma spectroscopy to identify individual radionuclides (noble gases). Noble gases have been detected almost exclusively in the reactor building effluent.

As necessary to supplement grab sampling at the Reactor Building Exhaust RIenum, samples are taken from the Offý6s Vhit Pipe samf lipi, rbhmlly 6f) the same frequency as RB Exhaust Plenum samples. The Offgas Vent Pipe sample point is upstream of the RB Exhaust Plenum and noble gases are more concentrated at this point. Dilution factors are applied to Offgas Vent Pipe noble 12./07 gas sample concentrations when the same nuclides are detected in both locations so' that concentrations detected in RB Exhaust Plenum samples may be compared to concentrations based on Offgas Vent Pipe samples; the more conservative concentration values are used in release calculations.

For containment purges and containment ventings when monitoring is alarming or not FUNCTIONALLY CAPABLE, samples are collected prior to the initiation of the release and, for long releases, periodically throughout the release (see ODCM Section 7.2.1). When detected activity concentrations are above a pre-determined threshold, these samples are evaluated using Equations (7-4) and (7-5), using release rates applicable to the vent/purge condition and taking continuous releases into account, to ensure that the site boundary dose rate limits of ODCM 3.11.2.1 are not exceeded. If the primary Containment atmosphere has equilibrated with the reactor building atmosphere, vent/purge sampling and analysis is not required. Such equilibrium with the drywell atmosphere may be considered to be established after at least one of the drywell equipment hatches has been open for 8 hours9.259259e-5 days 0.00222 hours 1.322751e-5 weeks 3.044e-6 months , and equilibrium with the torus atmosphere may be assumed after at least one torus hatch has been open for 8 hours9.259259e-5 days 0.00222 hours 1.322751e-5 weeks 3.044e-6 months .

As required by ODCM Table 4.11.2.1.2-1, special samples are required of the RB Exhaust Plenum and SGTS following shutdown, startup or a THERMAL POWERchangeexceeding 15% within a 1 hour1.157407e-5 days 2.777778e-4 hours 1.653439e-6 weeks 3.805e-7 months period. Exceptions to this special samrpiing are allow.ed as noted prvosyin r00CMN qpntinn 7 9 9 FERMI 2 ODCM - TRM VOLUME I7 7-10 Rev. 18

7.6 Calculation of Activity Released The following equation may be used for determining the release quantities from any release point based on the sample analysis:

Qi =. OE + 03

VF

T* Ci (7-8)

Where:

Qi = total activity released of radionuclide i (pCi)

VF Ventilation System release rate (liters/min)

T = total time of release period (min) 1.0 E + 03 milliliters per liter Ci = concentration of radionuclide i as determined by analysis of the sample (pCi/cc). For noble gas grab samples, this value may be corrected for variations during the release period by multiplying by the ratio of the average noble gas monitor reading during the release period to the reading at the time the sample was taken.

For iodine and particulate samples, this value should be corrected for decay during the sampling period, for sample line loss if adequate data are available, and for collection efficiency if a significant fraction of the material to be collected passes through the collection media. For all samples, this value should be corrected for decay between sample collection and counting and for decay during counting.

7.7 Site Boundary Dose Rate - Radioiodine and Particulates ODCM 3.11.2.1.b limits the dose rate to <1500 mrem/yr to any organ for 1-131, 1-133, tritium and particulates with half lives greater than 8 days. To demonstrate compliance with this limit, an evaluation is performed at a frequency no greater than that corresponding to the sampling and analysis time period (nominally once per 7 days). The following equation may be used in the dose rate evaluation for 1-131, 1-133, and particulates with half lives greater than 8 days:

DRZ= (%I/ 0* RI-13

VF,* 16.7 *ZIci (7-9)

Where:

FERMI 2 ODCM - TRM VOLUME II 7-11 Rev. 13

DR = total maximum organ dose rate for all release points (mrem/yr)

/Q Q, = atmospheric dispersion factor for release point r to the controlling SITE BOUNDARY location (sec/m3 ) from Table 7-3 or plant procedures R1-131 = 1-131 child thyroid inhalation pathway dose factor (mrem/yr per pCi/m 3 )

from Table 7-4 VFr = Average ventilation flow for release point r during release period (liters/min)

Cir = Concentration of radionuclide i (1-131, 1-133, or particulate with half life greater than 8 days) released from release point r during the appropriate release period (pCi/cc)-usually determined by gamma spectral analysis of effluent sample and corrected as described in definition of C, in section 7.6 16.7 = 1000 cc/liter

0.0167 min/sec Release periods used in Equation (7-9) are the most recent periods evaluated for the different release points, and these periods may not be identical.

Alternatively, the site boundary dose rate may be evaluated using the highest individual isotopic dose factors for all age groups to calculate inhalation and ground plane exposure at the highest dispersion factor location at or beyond the site boundary, as well as vegetation, milk, and meat exposure at the garden, milk, and meat locations with the highest deposition factors. Dose rate due to tritium is currently evaluated by this method, and when tritium has been detected in gaseous effluents during the most recent release period, the tritium dose rate must be added to the result from Equation (7-9) to evaluate compliance with ODCM 3.11.2.1.b.

The dose rate evaluation described above may have to be performed more frequently than once per week in order to meet the requirements of ODCM Table 4.11.2.1.2-1, footnote g: Daily sampling is required following startup, shutdown, or thermal power changes exceeding 15% in one hour ifthe applicable noble gas effluent monitor reading has increased by a factor of 3.

FERMI 2 ODCM - TRM VOLUME II 7-12 Rev. 14

( Noble Gas Effluent Dose Calculations - 10 CFR 50 7.8 7.8.1 UNRESTRICTED AREA Dose - Noble Gases ODCM.4.11.2,.2 requires that an assessment of releases of noble gases be performed at least once per 31 days to evaluate compliance with the quarterly dose limits of 5 mrad, gamma-air and 10 mrad, beta-air and the calendar year limits 10 mrad, gamma-air and 20 mrad, beta-air. The following equations may be used to calculate the gamma-air and beta-air doses. If noble gases are detected at multiple release points, these equations must be performed for each such release point, and the calculated air doses must be summed.

D, = 3.17E-O08* /Q* / (M *QJ)

(7-10) and D,6 = 3.17E -08 zIQ* (N

QJ)

(7-11)

Where:

= air dose due to gamma emissions for noble gas radionuclides (mrad) air dose due to beta emissions for noble gas radionuclides (mrad)

= atmospheric dispersion to the controlling SITE BOUNDARY location (sec/m3 )

cumulative release of noble gas radionuclide i over the period of interest (pJCi)

= air dose factor due to gamma emissions from noble gas radionuclide i (mrad/yr per lJCi/m 3, from Table 7.0-2)

= air dose factor due to beta emissions from noble gas radionuclide i (mrad/yr per PCi/M 3, Table 7.0-2) 3.17 E - 08 = 1/3.15 E + 07 (year/sec)

Note: Page content was last changed with ODCM Revision 15.

FERMI 2ODCM - TRM VOLUME !f 74t-3 e---2-1/or

-;.-W

7.9 Radioiodine and Particulate Dose Calculations - 10 CFR 50 7.9.1 UNRESTRICTED AREA Dose - Radioiodine, Particulates, and Tritium In accordance with requirements of ODCM 4.11.2.3, a periodic assessment (at least once per 31 days) is required to evaluate compliance with the quarterly dose limit of 7.5 mrem and the calendar year limit of 15 mrem to any organ. The following equation may be used to evaluate the maximum organ dose due to releases of 1-131, 1-133, tritium, and particulates with half-lives greater than 8 days:

D,,= Z.(W,

SFP

3.17E - 8

Rip,,

Qr) p r i (7-14)

Where:

Dao dose or dose commitment to Organ o of age group a (identified in Table 7.0-3 or plant procedures)

Wr = atmospheric dispersion parameter for release point r and the residence location identified in Table 7.0-3 or plant procedures.

Either:

a) X/Q, atmospheric dispersion for inhalation pathway and H-3 and C-14 dose contribution via other pathways (sec/m3 ), or b) D/Q, atmospheric deposition for vegetation, milk and ground plane exposure pathways (m- 2 )

Raipo dose factor (mrem/yr per piCi/m 3 ) or (m2 - mrem/yr per pCi/sec) from Table 7.0-4 for radionuclide i, age group a, pathway p, and organ o as identified in Table 7.0-3 or plant procedures. Values for Raipo were derived in accordance with the methods described in NUREG-0133. As noted in NUREG-0133 section 5.3.1.3, in the case that the milk animal is a goat, parameter values from Reg Guide 1.109 should be used. For 1-131, for example, use of the goat feed/forage consumption rate given in Table E-3 and the stable element transfer factor given in Table E-2 of Reg Guide 1.109 results in grass-goat-milk dose factors which are equivalent to the grass-cow-milk dose factors in Table 7.0-4 multiplied by 1.2.

Note: Page content was last changed with ODCM Revision 15.

FERMI 2 QDCM - TRM VOLUME 11 7-14 Rev. 18l

Qir cumulative release from release point r over the period of interest (normally one month) for radionuclide i 131, 1-133, tritium or radioactive material in particulate form with half-life greater than 8 days (pCi).

SFp annual seasonal correction factor to account for the fraction of the year that the applicable exposure pathway does not exist:

1) For milk and vegetation exposure pathways:

0.5 (derived from Reg Guide 1.109, Rev 1. A six month fresh vegetation and grazing season (May through October) limits exposure through this pathway to half the year.

2) For inhalation and ground plane exposure pathways:

= 1.0 (derived from Reg Guide 1.109, Rev 1) 3.17 E-8 = 1 / 3.15 E7 (year/sec)

This equation should be used to evaluate organ doses for the individual with the highest potential offsite dose. This calculation is performed monthly and is added to previous results for the quarter and year. The highest quarterly and annual cumulative organ dose totals for this individual should be compared with the limits of ODCM 3.11.2.3.

The residence, age group, and relevant exposure pathways for this individual are listed in Table 7.0-3 and in plant procedures. Plant procedures may provide updated information which differs from Table 7.0-3. This individual is identified from data obtained in the annual Land Use Census (ODCM 3.12.2).

FERMI 2 ODCM - TRM VOLUME I5 7-15 Rev. 13

7.10 Gaseous Effluent Dose Projection As with liquid effluents, the Fermi 2 ODCM controls on gaseous effluents require "processing" of gaseous effluents if the projected dose exceeds specified limits. These controls implement the requirements of 10 CFR 50.36a on maintaining and using the appropriate radwaste processing equipment to keep releases ALARA.

ODCM 3.11.2.5 requires that the VENTILATION EXHAUST TREATMENT SYSTEM be used to reduce radioactive material levels prior to discharge when the projected dose exceeds 0.3 mrem to any organ in any 31 day period (i.e., one-quarter of the design objective rate). Figure 7.0-1 presents the gaseous effluent release points and the VENTILATION EXHAUST TREATMENT SYSTEMS applicable for reducing effluents prior to release.

Dose projection is performed at least once per 31 days using the following equation:

Dmaxp= Dm..*(31/d)

(7-16)

Where:

Dmaxp maximum organ dose projection for the next 31 day period (mrem)

NOTE: The reference calendar quarter is normally the current calendar quarter. If the dose projection is done in the first month of the quarter and is to be based on dose calculated for the previous quarter, the reference calendar quarter is the previous quarter.

Dmax the cumulative maximum organ dose from the beginning of the reference calendar quarter (normally the current quarter) to the end of the most recently evaluated release period as determined by Equation (7-14) or (7-15) (mrem) d = number of days from the beginning of the reference calendar quarter to the end of the most recently evaluated release period.

31 number of days. in projection FERMI 2 ODCM - TRM VOLUME 11 7-16 Rev. 13

TABLE 7.0-1 Values for Evaluating Gaseous Release Rates and Alarm Setpoints Allocation Allocated Dose Release Point Flow Rate Factor Rate Limit (liter/min) (AF) (mremlyear)

Reactor Building 2.67E6 0.50 T Body = 250 Exhaust. Plenum Skin = 1500 D1 -P280 Organ = 750 Standby Gas 1.07E5 0.10 T Body = 50 Treatment. System Skin = 300 Div I D11-P275 Organ = 150.

Standby Gas 1.12E5 0.10 T Body= 50 Treatment System Skin = 300 Div II D11-P276 Organ = 150 Turbine Building 8-67E6 0.20 T Body = 100 Ventilation Skin = 600 D11 -P279 Organ = 300 Radwaste Building 1.13E6 0.02 T Body= 10 Ventilation Skin = 60 D1 -P281 Organ = 30 Onsite Storage 3.06E5 0.02 T Body= 10 Building Skin = 60 Ventilation Organ = 30 D11-P299 1 3/07 Reactor Building 2.57E6 0.50 T Body 125 Ventilation* Skin = 750 Gulf Atomic Organ = 375 Monitors D11-N408, N410 D 11-N408 and N410 will start the SGTS, close the Drywell PurgeNent Valves, isolate Rx Building Ventilation System, isolate Control Center, and initiate emergency recirculation mode.

Note: Page content was last changed with ODCM Revision 17.

-Rev.18 ......

FERMI 2 ODCM - TRM VOLUME 7-17 R.

TABLE 7.0-2 6F Dose Factors for Noble Gases*

Total Body Skin Gamma Air Beta Air Gamma Dose Beta Dose Dose Factor Dose Factor Nuclide Factor Ki Factor Li Mi Ni (mrem/yr per (mremlyr per (mradlyr per (mradlyr per pCilm 3 ) pCilm 3 ) pCilm 3 ) pCilm 3 )

Kr-83m 7.56E-02 1.93E+01 2.88E+02 Kr-85m 1.17E+03 1.46E+03 1.23E+03 1.97E+03 Kr-85 1.61E+01 1.34E+03 1.72E+01 1.95E+03 Kr-87 5.92E+03 9.73E+03 6.17E+03 1.03E+04 Kr-88 1.47E+04 2.37E+03 1.52E+04 2.93E+03 Kr-89 1.66E+04 1.01 E+04 1.73E+04 1.06E+04 Kr-90 1.56E+04 7.29E+03 1.63E+04 7.83E+03 Xe-131m 9.15E+01 4.76E+02 1.56E+02 1.11E+03 Xe-1 33m 2.51 E+02 9.94E+02 3.27E+02 1.48E+03 Xe-133 2.94E+02 3.06E+02 3.53E+02 1.05E+03 Xe-135m 3.12E+03 7.11E+02 3.36E+03 7.39E+02 Xe-135 1.811E+03 1.86E+03 1.92E+03 2.46E+03 Xe-137 1.42E+03 1.22E+04 1.51E+03 1.27E+04 Xe-138 8.83E+03 4.13E+03 9.21 E+03 4.75E+03 Ar-41 8.84E+03 2.69E+03 9.30E+03 3.28E+03 NOTE:

Dose factors taken from NRC Regulatory Guide 1.109 FERMI 2 ODCM - TRM VOLUME II 7-18 Rev. 13

TABLE 7.0-3 Controlling Locations, Pathways, and Atmospheric Dispersion for Dose Calculations*

ODCM Control Location Pathway(s) Controlling Age Group zr/Q DIQ (seclm 3) (1ra2 )

3.11.2.1a site boundary noble gases N/A RB: 1.25E-6 N/A (0.57 mi, NW) direct exposure TB: 5.71E-6 RW: 2.66E-6 3.11.2.1b site boundary inhalation child RB: 1.25E-6 N/A (0.57 mi, NW) TB: 5.71E-6 RW: 2.66E-6 3.11.2.2 site boundary gamma-air N/A RB: 1.25E-6 N/A (0.57 mi, NW) beta-air TB: 5.71E-6 RW: 2.66E-6 11.2.3 residence vegetation child RB: 1. 1OE-6 1.59E-8 (0.67 mi, inhalation, and TB: 4.02E-6 3.06E-8 WNW) ground plane RW: 1.53E-6 1.76E-8 NOTE: *The identified controlling locations and pathways are derived from land use census data and dispersion and deposition factor data tables. The dispersion and deposition factor values listed are conservative values; they represent the highest annual average values seen at that location for a period of several years.

FERMI 2 ODCM - TRM VOLUME II 7-19 Rev. 13

Table 7.0-4 Gaseous Effluent Pathway Dose Commitment Factors Raipo, Inhalation Pathway Dose Factors - ADULT 3

(mrem/yr per UlCi/m )

muclide Bone Liver Thyroid Kidney Lung GE-Lit T. Body 1.26£E3 1.26E+3 1.26E+3 I. 26E- 3 1. 26E+3 1.26E£3 H-3 3.41E-3 3.11E+3 3.41E-3 3.41E-3 3.4 IE+3 3.6 1£+3 C- '1 1.82£E4 i.02£.'4 1. 02£E- 1.02£E4 1.02E-4 1.02£E4 1. 02E+4 1.02E£4 NA-2'.

P-32 1. 32£E-6 7.71£+4 S. 64E+ 5.01£E4 Cr-Si S. 95£..I 2. 28E+ 1 1. 4£.E4 3. 32£t3

3. 96E-4 9.84E-3 1. 40E÷6 7.74E-4 6. 30E-3 Mn-S4 1.83E-1 mfn-56 1. 24E-0 1.30E.0 9. 44*£3 2.02E-4

2. 4bE'. 7. 21£+4 6.03E+3 3.94E-3 Fe-55 I. 70£E'4 I. 18E-4 2. 78E.4 1. 02E.6 1. 88£. 5 1.06E'4 Fe-59

6. 92E.2 3. 70£.5 3. 14E.4 6.7 1E+2 Co-57 1.SSE- 3 9. 28E-:5 1.06£-.S 2.07E- 3 Co-58

1. 155E£4 5. 97E.6 2.85E+S 1.48£E.

Co-bO

4. 32E-5 3. 14E..4 1. 78£+5 1.34E÷4 1.54 SE.4 Ni-63

1. 54E+O 2. IOE-I S.60£+3 I.23E-+4 9. 12E-2 Ni-65

1. 46E-0 4 .62E-0 6. 7BE£3 4.90£E' 6. 1S-I CU-64

3. 24 E4 1.03£.S 6. 90£-4 8, 64£+5 5. 34£,4 4. 66E.4 Zn-65

3. 38E-2 6. 51£-2 6. 22£-2 9. 20£E2 1.63E£+1 4. 52£-3 Zn-69 1.04£E4 1. 35£.4 Br-82 2.32E-2 2.£4 I.2 Br-83

1. 64£-3 3.13E£2 Br-84 1.28£EI Br-÷85

1. 35£E 5 1.66E-4 5. 90E-4 xb-86 Rb-B8 3.871+2 3.34£-9 1. 93£E2

2. 56E+ 2 1.70£E2 Rb-89 3.04E£ 5 1.40E-6 3. 50E S B. 72E-3 sr-89 9.92E'*7 9.60E+6 7.22E. 5 6. 10£+6 Sr -90 91

6. 19r.+1 3.65£E4 1.91E. 5 2. 50£E0 Sr-5r-92 6. 74E+0 1.6SE-4 4. 30£.4 2.91E-I 2.09E+3 1. 70E+ 5 5. 06£.5 5. 6 1E+ I Y-90 Y-91. 2.61£-I 1.92E+3 1. 33E,0 i.02E-2 Y-91 4 .62E-5 I. 70E-6 3. 85E. S 1.24E-4 Y-92 I .03E- I 1, 57E-4 7. 35£+4 3.0ZE-I

9. 44E. I 4. 85E.4 4. 22£E5 2.6 1£E0 Y-93 I .07E+5 3.44£E4 5. 42E+4 1.77E+6 1. 50£+S 2. 33E+4 Zr-95 9

9. 68£' I 1. 96E+1 2.97E- I 7 .87£+4 S. 23E+ 5 9.04E.0 Zr- 7

i. 41E-'. 7.8M+3 1.OI.£+5 4. 21£E3 Nb-g5 7.724£+1 S. 05E+S

2. 22£- 1 6. 541-2 2. 40E+3 2.42E£2 2. 05E-2 Nb-97 5. 62E-2

1. 21E+2 2.91£E2 9. 12£E-4 2. 48E+S 2. 30£. 1 Mo-99 t .03£-3 2.91£-3 4.42£-2 7.64E-2 A. 16E+3 3.70£-2 TC-99.

4. 18£-5 6.02£-5 1.08£-3 3. 99E£2 5.90£-A Tc-101 Ru-103 I 53E-3 S. 83£E3 5. 05E+5 1. 10£÷S 6. 58£E2 Au- 105 7. 90£- 1 1.02L.0 1. ICE-. 4. 82E.4 3.11E-I RAu-106 6.91 E*4 1.34E.5 9. 36£E6 9. 12E 5 B. 72£)3 Rh-1O3M Rh-106 Ajl- 110- 1 . OBE-t, 1. 0OE£4 1.97£.4 4. 63E-6 3.02£E 5 5.94 E+3 5b-124 3. 12E-4 S.89E-2 7.55£E 1 2.48E-6 4. 06£. 5 1.24E-4 Sb-12S 5. 36E£.. S. 95E-2 S. 40E- I 1.74E+6 1. 01£. 5 1.26E-'.

Te-125S 3. 42£E3 1. 58E+3 1.OSE+ 3 1.24E£4 3. 14£E5 7. 06E.4 4.67E.2 Te- 127o 1.26£.4 5. 77£+3 3.29E£3 '..58£". 9, 60E. 5 1. 50E.5 1. 57E.3 Te- 127 1.40E÷O 6.42£-I 1. 06E+0 S. 10E-0 6. 51E,3 5. 74£E4 3. 10E-I Te- 127 9. 76E£3 3.66E£4 I. 16L.6 3.83t+S 1. S8£.3 4.67£-3 3. 44£-3 Tc-129 4. 98£-2 2.39£-2 3. 90E-2 1.87E-1 1.94£.3 I.57£+2 1. 24E-2 Te- 131o 6.99E- I 6.36E. 1 5.50£' 1 3. 09E+2 1.4Cr.E 5. 56E÷5 2. 90£. I Te- 131 5. 95E-3 9. 36£-3 4.37£-2 1.39E.3 1. 8E.1 3. 59£-3 I . I IE-?2 2 2.88E.5 S. 10E5 i. 62£D2 Te-13 2.60E?2 2. 15.E 2 1,90£.2 1. 46£.3 1-130 4. 58E+ 3 1.34£'4 1.14E+6 2.09£.'. 7.69E-3 5.28£+3) 1-131 2. 52£'4 3. 58£64 1, 19E.7 6. 13£-4 6.28E+3 2. 05£.4 1-132 I. 16E-3 3.26E.3 I. 14£.5 S. 18E.3 4.06E#2 1. 16£E3 1-133 8. 64Z-3 1.48£.-' 2.15Eb 2. 581.4 8.88E.3 4. 52E-3 7-20 Rev. 13 FERMI 2 ODCM - TRM VOLUME II

Table 7.0-4 Gaseous Effluent Pathway Dose Commitment Factors Raipo, Inhalation Pathway Dose Factors - ADULT (cont.)

3 (mrem/yr per UCi/m )

muclide Done Liver Thyroid Kidney Luna GI-LLU T.Body 1-134 6.44E-2 1.73E-3 2.98E.4 2.75E-3 - 1.01E.0 6.15E.2 1-135 2.68E+3 6.98E-3 4.,8E,5 1.11E-4 - 5.25E3 2.57E-3 Cz-134 3.73E÷5 8.48E5 - 2.87E-5 9.76E-4" 1.04E÷4 7.28E÷5 Cs-136 3.90E-4 1.46E.5 - 8.56E+4 1.20E-4 1.17E-4 1.10E-5 Cc-137 4.78E-5 6.21E-5 - 2.22E.5 7.52E.4 8.40E.3 4.28E,5 C.-138 3.31E+2 6.21E-2 - 4.8OE2 4.86E.1 1.86E-3 3.24Ei2 Ba-139 9.36E-1 6.66E-4 - 6.22E-4 3.76E+3 8.96E-2 2.74E-2 Ba-1'O 3.o0WE4 4.90E-1 - 1.67E.1 1.27E,6 2.18ES+ 2.57E£3 Ba-141 1.OOE-1 7.53E-5 - 7.OOE-5 1.94E-3 1.16E-7 3.36E-3 Ba-142 2.63E-2 2.70E-5 - 2.29E-5 1.19E-3 - 1.66E-3 La-140 3.44E÷2 1.74E+2 - 1.36Ei5 4.58E÷5 4.58E,1 L"-142 6.83E-1 3.1OE-1 - - 6.33E-3 2.1iE+3 7.72E-2 Ce-1i¶ 1.99E+4 1.35E-1 - 6.26E-3 3.62E+5 1.20E+5 1.53E+3 Ce-143 1.86E-2 1.38E-2 - 6.08E.1 7.98E*4 2.26E-5 1.53L-l Ce-14i 3.43E-6 1.43E+6 - 8.48E.5 7.78£E6 8.16E.5 1.84E+5 Pr-143 9.36E.3 3.75E,3 - 2,16E-3 2.81ES 2.00E-5 4.64E-2 Pr-144 3.01E-2 1.25E-2 - 7.O5E-3 1.02E+3 2.15E-8 1.53E-3 Nd-14 5.27E.3 6.10E-3 - 3.56E+3 2.ZIE÷5 1.73E+5 3.65E+2 W-18? 8.48E+O 7.08E.O - - 2.90E+4 1.55E.5 2.48E+O Np-239 2.30E.2 2.26t.1 - 7.OOE+1 3.76E+4 1.19E.5 1.24E÷1 FERMI 2 ODCM - TRM VOLUME II 7-21 Rev. 13

Table 7.0-4 Raipo, Inhalation Pathway Dose Factors - TEENAGER 3

(mremlyr per gCi/m )

Nucl idc Boat Liver Thyroid Kidney Luns G1-LLI T. Body W-3 1.27E+3 1.27E+3 1.27E+3 1.276+3 1.27E+3 1.27E+3 C-"1. 2. 60E÷4 4. 87E.3 4. 87E.3 4. 97E+3 4.87E.3 4. 87E.3 4.87E-3 Na-24 1. 38E+4 1. 38E-4 1. 386.4 1. 38E-4 1. 38E+4 1. 38E.4 1.38E64 P-32 1.89E+6 i. 106.5 9. 28E64 7.16E-4 Cr-5 1 7. 50E.1 3 .07E. I 2. 10E-4 3.00E-3 1.35E62 Mn-54 5. 11E+4 1. 27E,4 1. 98E56 6. 68E+4 8. AG0+3 Hn-56 1.70E6O 1. 79E.0 1. 52E-4 5. 746-4 2. 52£-i Fe-5S 3. 34E.4 2. 38E.4 1. 24E.5 6.39E-3 5.546£÷3 Fe-59 1. 59 1.4 3. 70E.4 1. 53E.6 1.78E-5 1.43E-4 6.92E÷2 5.56£-5 3. 146.4 Co-57 9.20E62 Co-58 2. 07E+3 1. 34E-6 9.52E*4 2. 78E+3 Co-60 1.51E-4 8. 72E46 2.59E+5 1 . 98E.4 Ni-63 5. 8OE6. 4. 34E+4 3. 07E#5 1.42E+4 1.98E-4 Ni-65 2. 186E0 2. 93E-1 9. 36E-3 3. 67E+4 1.27E-i Cu-64 2.03E*0 6.4 16E0 1. 1 1E-4 6.146E4 8.48E-1 Zn-65 3.8566.' I. 34E+5 8. 64E-4 1. 24E+6 4. 66E-4 6. 24E-4 9

Zn-6 4.83E-2 9.20E-2 6.02E-2 1. 58E-3 2.856E2 6. 46E-3 Br-82 1 . 82E+4 Br-S3 3. 44E-2 Br-84 4.33E*2 Br-85 1.836+1 Rb-86 1. 90E+5 1.77E+4 8.40E.4 Rb-08 5. 466E2 2.92E-5 2. 72E62 Rb-89 3. 52E.2 3. 38-7 2. 331.2 Sr-89 4. 34E.5 2. 42E+6 3.7 1E'5 i .25E-4 Sr-90 1.08E-8 1. 65E.7 7.656E5 6.686E6 Sr-91 a.80E.. 1 6.07E*4 2.59E65 3.51E*0 Sr-92 9. 521.0 2. 74E64 1.19E65 4.06E-1 Y-90 2. 98E÷3 2. 93E-5 5.59E.5 8.00E+1 Y-91. 3.70E-1 3. 20E+3 3.02E- 1 1.42E-2 Y-91 6.61E+5 2. 94E+6 4 .09E-5 1. 77E-4 Y-92 1.476-1 2. 68E54 1.65E+5 4.29E-I Y-93 i .35E+2 8.32E+4 5. 79E6 5 3.72E+0 Zr-95 1. 46E+5 4.5864 6.74E+4 2. 696+6 1.49E+5 3.15E64 Zr-97 1.38E62 2. 72E+ I 4.12E-I 1. 30E+5 6. 30.-5 1.26E.1 Hb-95 1. 86E.4 1.03E+4 1.006*4 7.51E*5 5.66E+3 9.68E-4 Nb-97 3. 14E-1 7.78E-2 9.12E-2 3. 93E63 2.17E-3 2. 84-E-2 Mo-99 1.69E+2 4.11E+2 1. 541.5 2. 6 9E5 3. 22E6 1 Tc-99. 1.38E-3 3. 86E-3 5. 76E-"2 1.15E63 6.13E63 4. 99E-2 Tc-101 5.92E-5 8.40E-5 1.52E-3 6.67E+2 8. 72E-7 8.24E-4 Ru-103 2. 10.-3 7.43E-3 7. 83.5 1.09E+5 8. 96E-2 Ru- 105 1. 12E-0 1.41E60 1.82E*4 9.04E-4 4.34E-I Ru- 106 9.84E64 1.90£*5 1. 61E-7 9.60E65 1.246*4 Rh- 103.

Rh-106 A4z-11m 1. 3SE-4 1.316E+4 2.5OE64 6.75E+6 2.73E-5 7. 99E63 Sb- 124 4.30E.4 7.94E*2 9.76E-1 3. 85E÷6 3. 986. 5 1.686E4 Sb-125 7.38E+4 8. 08E6 2 7.04E61 2. 74E-6 9. 926.4 1.72E-4 Te- 12 S. 4. 88E 3 2.24E*3 1.40E+3 5. 36E65 7.50E.4 6.67E-2 Te-127a 1. 8OE04 8. 16E+3 4.386-2 6. 54E.4 1.66E-6 1.59E-5 2. 18E-3 Te-127 2.01£*0 9.12f-1 1.42E-0 7.28E.0 1.12E64 8.08E*4 4.42E-1 Te-1 29m I. 39E-4 6.58E*3 4.58E-3 5. 19E64 1. 98E+6 4.05E.5 2. 256E3 Te-129 7. 10E-2 3. 386-2 5.186-2 2. 66E- 1 3.30E+3 1. 62E+3 1.76E-2 Te-131. 9. 84E. 1 6.01E,1 7.256. I 4.39E+2 2.386*5 6. 216.5 4. 02E, I Te-131 1. 58E-2 8.32E-3 1.246-2 b.18E-2 2.34E+3 1.51E,1 5. 04E-3 Te-I132 3. 60E. 2 2.90E62 2.46E.2 1.95E63 4.49E. 5 4. 636- 5 2. 19E-2 1-130 6.24 . 3 1. 79E.4 1.49E*6 2.75E+4 9. V26*3 7.17E-3 1-131 3. 54 E.4 4. 91E-4 1.46E-7 8.40E-4 6.49E-3 2. 64E-6 1-132 1. 59E+3 4.38E63 1.51E. 5 6.92E*3 1.27E-3 1. 58E-3 1-133 1.22E+4 2. 0 564 2.92E+6 3. 59E.4 1.03E-4 6. 22E.3 FERMI 2 ODCM - TRM VOLUME II 7-22 Rev. 13 I

Table 7.0-4 Raipo, Inhalation Pathway Dose Factors - TEENAGER (Cont.)

3 (mrem/vr per U/Ci/m )

Done Liver Thyroid Kidney Lung GI-LLI T. body Nuclide 8.B8E.2 2.32E.3 3.95E-4 3.66E+3 - 2.0E+1 S.AGE.2 1-134 9.44E+3 6.21E.S 1.49E-4 - 6.95E-3 3.49E43 1-135 3.7OE.3 5.02E.5 1.13E,6 - 3.75E.S 1.46E+5 9.76E*3 5.49E-5 Cs-134 5.15E.4 1.94E,5 - 1.10E+S 1.7BE.4 1.09E-4 1.37E+5 Cz-136 6,70F-5 6,48E+5 - 3.04E*S 1.21E-5 8.48E,3 3.11E-5 Cs-137 4.66E42 8.56E÷2 - 6.62E?2 7.B7E+1 2.70E-1 4,46E-2 Ct-118 1.34E.0 9.44E-4 - 8.88E-4 6.46E+3 6.5SE.3 3.90E-2 Ba-139 6.70E, - 2.28E.i 2.03E+6 2.29E£5 3.52E-3 BS-140 5,47E-4 1.06E-4 - 9.84E-5 3.29E+3 7.46E-4 4.74E-3 B4-141 1.42E-1 3.70E-5 - 3.14E-5 1.91E.3 - 2.27E-3 sa-142 3.70E-2 4.79E+2 2.36E+2 - - 2.14E+5 4.87E.5 6.26E-1 LA-140 9.60E-1 4.25E-1 - - 1.02E+4 1.20E+4 1.06E-1 LA-142 2.84E+4 1.90E+4 - 8.88E+3 6.14E+5 1.26E+5 2.17E.3 Ce-1hi 1.94E+2 - 8.64E+i1 1.30E*5 2.5SE+5 2.16E+1 Ce-1h3 2.66E.2 4.89E.6 2.02E+o - 1.21E+6 1.34E-7 8.64E+5 2.62E-5 Ce-hi 1,34t+4 5.31E-3 3.09E*3 4.93E+5 2.14E,5 6.62E+2 Pr-143 1.76E-2 1.01E-2 1.75E-3 2.35E-4 2.1BE-3 Pr-144 4.3OE-2 7,86E.3 8.56E+3 - 5.02E£3 3.72E+5 1.82E+5 5.13E+2 Kd- 47 1.20E+1 9.76E÷O - - 4.74E+4 1.77E.5 3.43E+O W-187 3.38E.2 3.19E+1 - 1.OOE+2 6.49E+4 1.32E15 1.77E+i Np-239 7 -23 Rev. 13 FERMI 2 ODCM - TRM VOLUME II

Table 7.0-4 Raipo, Inhalation Pathway Dose Factors - CHILD

( (mrem/yr per jICi/m )

3 Huct ide Bone Liver Thyroid Kidney Luns Gi -LL1 T.Body H-3 1.12£+3 1. 12E+3 1 .12E-3 1. 12E-3 1. 12E+3 1. 12E-3 C- 14 3.59"E-4 6. 73E+3 6. 73E.3 6. 73£+3 6.73E- 3 6. 73E÷3 6. 73E+3 Na-24 1.61E£4 1.61 E 4, 1.61£E4 1.61E-4 1.61£E.4 1.61E-4 1.61Ev4 P-32 2. 6OE'6 1.14.,5 4.22£-4 9.88Ev4 Cr-S1 8. 5SEv1 2. 43£E I 1. 70£-4 I .08E+3 1. 54E+2 Mn- 54 4. 29£.4 1.00£'.'. 1 . SBE+6 2. 29E+4 9. 51E.3 mn-56 1. 66£E0 1. 67 E0 1. 31£.E4 1.23E.5 3.12E-1 Fe-S5 4. 74E£- 2. 52£E4 1. 11E.5 2.87E-3 7.77E.3 Fe-59 2.07£-4 3. 34E.4 1. 27E+6 7.07E+4 1.67E£4 Co-S7 9.03E+2 5. 07£-5 1. 32E÷4 1.07E+3 Co-SB 1.77E-3 1. 11 E6 3.44£E- 3. 16E+3 Co-60 1. 31E-4 7. 07E-6 9.62E-4 2. 26E-4 Ni-63 8. 21 E+5 4. 63E.4 2.75X+5 6. 33E+3 2.80E+4 Ni-65 2.99Z+0 2. 96E-I S. 18E*3 S. 40E-4 1.64E-1 Cu-64 1. 99E+0 6.03E-0 9. 58E.3 3.67E+4 1.07E÷o Zn-65 4. 26E+4 1. 13E- 5 7.14E+4 9. 95E-5 1.63E.4 7.03£.4 9

Zn-6 6. 70E-2 9. 66E-2 5.85E-2 1. 42E+> 1.02E+4 8 .92E-3 Br-B2 2.09E£4 Br-83 4. 74E+2 Br-84 5. 4 8E2 Br-85 2. 53E+1 Rb-96 I. 98£+ S 7.99E+3 1. 14EvS Rb-BB 5. 62E£.2 1.72£E1 3.66E.2 Rb-B9 3.445E2 1.89E+0 2. 90E+2 sr-89 5. 99E. 5 S2.16E.6 I. 67E+5 1.72E-4 Sr-90 1.01E.9 1.48E+7 3.43E+5 6. 44E+6 sr-91 1. 21E.2 S.33E+4 1. 74E.S 4. 59£+O Sr-92 1. 31E+1 2. 40E.4 2. 42Ev5 5.25E-1 Y-90 4.11E+3 2.62E-5 2. 68E÷v 1. 1IEv2 Y-91m 5. 07£-1 2.8 1E-3 1.72E+3 1.894E-2 Y-91

9. 14E.S 2.63E+6 1.84E£5 2.44Ev4 Y-92 2.O.E-+1 2.39£E4 2.39Ev5 5.81£-1 Y-93 1. 86E+2 7.44E+4 3. 89E*5 S. I1E÷O Zr-95 I. 90E+ 5 4.18'E+4 5.96£E-4 2. 23E-6 6. 11£E-4 3.70£-4 Zr-97 I. 88E2 2.72£. I 3. 89£.i 1.13E+5 3.SI£ES 1 .60£+1 Wb-9 5 2.3 5E+4 9.18E+3 8.62E,3 6.14E+5 3. 70E-4 6. 55E3 Nb-97 4. 29E-1 7.70E-2 8. SSE-2 3.42E.3 2. 78E. 3.60E-2 Ho-99 1. 72E-2 3.92£E2 1. 35E*5 1. 27E+5 4.26Ev 1 Tc-99& 1.78E-3 3. 4BE-3 5.07E-2 9.51£+2 4.81E,3 5. 77E 1. 45E-3 5.85E*2 1. O8£-3 Tc-101 8. 10£-S 8. S1E-5 1 63E+1 Ru-103 2.79E+3 7.03E+3 6.62E-5 4.48E+4 1.07E+3 Ru-105 I . 53£÷O 1. 34E£0 1. 59E-4 9.95E£4 S. 55E-i 1.84E÷5 1. 43E+7 4. 29E- 5 1. 69£+4 Ru- 106 1. 36E+ 5 Rh-103m Rh- b06 AZ- 1100= 1.69E-4 1. 14E-£ 2.12E.4 5.48E÷6 1. OOE 5 9.14E.3 Sb- 124 S. 74E.4 7.40E+2 I. 26E+2 3.24E+6 2.00>E4 I. 64E÷S Sb- 125 9. 8 E+4 7. 59E+2 9. 10E+1 2.32E+6 4.03E+4 2.07£+4 Te-125. 6. 73E÷3 2. 33E-3 1. 92E-3 4. 77E÷S 3. 38E.4 9. 14E£2 Te-127. 2.49£E'4 8. SSE+3 6. 07£+3 6. 36E+4 1.48E+6 7. 14E+4 3. 02E+3 Te-127 2.777E>0 9.51E-I 1.96E+0 7.07E-0 1.00E+4 5. 62E.4 6.11£-i Te- 129m 1. 92E+4" 6.85E+3 6.33E+3 5.03E+4 1. 76E-6 1.82E+5 3.04E13 Te-129 9. 77E-2 3. 50E-2 7 . 14E-2 2.57E-i 2.93E-3 2.55E+4 2. 3BE-2 Te-131m 1. 34E.2 S.92E+1 9.77Ev1 4. 00£E 2 2. 06£. 5 3.08E+5 S.07E£ I Te-131 2. 17£-2 8.4E-3 1. 70E-2 5.88£-2 2.0 SE*3 1.33E-3 6. 59E-3 Te-132 4.81E-2 2.72E,2 3. 1 7E£2 1.77E-3' 3. 77E+5 1.38Ev5 2. 63E-2 1-130 B. 18E-3 1.64£.'. 1.85E-6 2.4 5E.4 5.1 1£+3 8.44E÷3 1-131 4.81E+4 4.81£.4 1.62E-7 7.88E.4 2. 84E+3 2.73£E.4 1-132 2. 12E£3 4.07E-3 1. 94E45 6. 25E. 3 3.20E-3 1 .88E13 1-133 I.66E+4 2.03E+4 3. 85E+6 3.38E+4 5.48E+3 7. 70£E3 FERMI 2 ODCM - TRM VOLUME II 7-24 Rev. 13 I

Table 7.0-4 Raipo, Inhalation Pathway Dose Factors - CHILD (Cont.)

3 (mrem/yr per u Ci/m )

muclide Bone Liver Thyroid Kidney LunS GI-LU T.gody 1-134 1.17E-3 2.16E-3 5.07E+4 3.30E+3 - 9.SSE+2 9.95E+2 1-135 4.92E-3 8.73E+3 7.92E+5 1.34E-4 - 4.44E-3 4.14E-3 C.-134 6.51E+5 1.01E-6 - 3.30E.5 1.21E#5 3.85E+3 2.25E-5 Cs-136 6.51E.4 1.71E ÷5 - 9.55E.4 1.45E-4 4.18E ÷3 1.16E -5 Co-137 9.07E*5 8.25E+5 - 2.82E+5 1.04E.5 3.62E£3 1.28E£5 Cs-138 6.33E+2 8.4OE+2 - 6.22E+2 6.81E.1 2.70E+2 5.SSE 2 Ba-139 1.84E.0 9.84E-4 - 8.62E-4 5.77E+3 5.77?E4 5.37E-2 Ba-140 7.40E+4 6.48E1 - 2.11E+1 1.74E+6 1.02E.5 4.33E+3 B*-U41 1.96E-1 1.09E-4 - 9.47E-5 2.92E+3 2.75E+2 6.36E-3 Ba-142 S.OOE-2 3.60E-5 - 2.91E-5 1.64E+3 2.74E.0 2.79E-3 L.a-140 6.44E+2 2.25E-2 - - 1.83EiS 2.26E÷5 7.55E-1 La-142 1.30E+O 4.11E-1 - - 8.70E3 7.59E+4 1.29E-1 Ce-141 3.92E+4 1.95E+4 - B.55E-3 5.44E+5 5.66E+4 2.90E+3 Ce-143 3.66E+2 1.99E÷2 - 8.36E+1 1.15E+S 1.27?E5 2.87E+1 4

Ce-14 6.77E+6 2.12E-6 - 1.17E+6 1.20E+7 3.89E+5 3.61E+5 Pr-143 1.85E-4 5.55£E3 - 3.00E+3 4.33E*5 9.73E-4 9.14E+2 Pr-144 5.96E-2 i.BSE-2 - 9.77E-3 1.57EL3 1.97E+2 3.OOE-3 Nd-147 1.08E4 9.73E+3 - 4..1£.3 3.28ES 8.21E-4 6.81E+2 W-187 1.63E+1 9.66EO - - 4.11£E4 9.10E-4 4.33E.O Np-239 4.66E+7 3.34E+1 - 9.73E+1 5.81E+4 6.40*E4 2.35EI.

FERMI 2 ODCM - TRM VOLUME II 7-25 Rev. 13

Table 7.0-4 Raipo, Inhalation Pathway Dose Factors - INFANT 3

(mrem/yr per gCi/m )

PNucl ide Bone Liver Thyroid Kidney Lung GI6-.LI T. body H-3 6. 47E.2 6. 47.-2 6. 47E.2 6;47E+2 6.47E* 2 6. 47E62 C- 14 2. 656.4 5. 31E+3 5. 31E.3 5.3 IE-3 5.31E-3 5. 31E.3 5.3 1E+3 Na-24 1.06E.4 1,06E.4 I .06E.4 1.06E,4 1.06E.4 1.06E64 1.06E.4 P-32 2.03E-6 1. 12E.5 1. 61E64 7. 74E+4 Cr-51 5. 75E.1 1. 32E-1 I . 28E.4 3. 57E-2 B. 95E+1 Mn-54 2. 53E.4 4. 98E. 3 I .OO+6 7.06E.3 4.98E+3 mn- 56 1. 546.0 1. 10E.0 I. 25E.4 7. 17E64 2.21E-1 Fe-55 1. 97E+4 1. 17E.4 8. 696.4 1.09E+3 3.33E+3 Fe-59 1. 36E.4 2. 35E.4 1. 02E+6 2.48£.4 9.48E.3 Co-57 6. 51E.2 3 . 796,5 4.86E+3 6.4 1E.2 Co-5B I. 22E63 7.77E.S I1.116.4 1.82E+3 Co-bO S. 02E-3 4.51E+6 3. 19E+4 1. 18E+4 Ni-63 3. 39E.5 2.04 E-4 2.09E-5 2. 42E+3 1. 16E.4 Pli-65 2. 39E÷0 2. 84E-1 B. 12E+3 5.01E+4 1. 23E-1 Cu-6d. 1. 8BEB0 3.98E+0 9. 30E,3 1. 50-.4 7.74E-I Zn-65 1. 93E.4 6. 26E÷4 3. 25E-4 6.4 7E.5 5. 14E.4 3.1 1E.4 9

Zn-6 5. 39E-2 9.67E-2 4 .02-2 1.47E÷3 1. 32E.4 7.-1B-3 Br-82 1. 33E-4 Br-83 3.B16E2 Br-84 4.OOE.2 Br-85 2. 04E-I Rb-B6 1. 90E+5 3. 04E.3 8. 82E,4 Rb-8B S. 57E+2 3. 39Z+2 2. 87E62 Rb-89 3.21E.2 6.82E61 2.06E+2 Sr-89 3. 98E-5 2.03E-6 6. 40E.4 1. 14E-4 Sr-90 4.096+7 1. 12E.7 1 . 31 Z+ 5 2.59E+6 1

Sr-9 9. 56E.1 5. 26E.4 7. 34 E+4 3.46E.0 1 .056.1 2. 38E.4 1. 40E.5 3.916-I Sr-92 Y-90 3. 29.+3 2.69E*5 I .04E6S 8.82E-1 Y-91M 4.07E-1 2. 79E-3 2.35E-3 1.39E-2 Y-91 S. BB6.5 2. 45E+6 7.03E.4 1. 57E.4 Y-92 1.64E 61 2. 45E.4 1.27E.5 4.6 1E-I Y-93 1. 50E.2 7. 64E64 1. 67E65 4.07E.0 Zr-95 1. 156.5 2. 79E+4 3.116E.4 1. 75E-6 2. 17E-4 2.03E.4 Zr-97 1. 50E+2 2. 56E.1 2. 596. 1 I. 106.5 1.40E.5 1. 17E.1 Nb-95 1. 57E.4 6. 43E-3 4.72E+3 4.79E- 5 1. 27E-. 3. 78E.3 Nb-97 3.42E-1 7. 29E-2 S. 70E-2 3. 32E 3 2.69E-4 2.63E-2 Plo-99 1. 65E.2 2. 656E2 1. 356.5 4.87E÷4 3. 23E- 1 Tc-99. 1. 4OE-3 2.B8E-3 3. 11E-2 B. 116.2 2.03E+3 3.72E-2 Tc-tO1 6.51E-5 B.23E-5 9. 79E-4 5. 84.*2 8.44E-2 B. 12E-4 Ru- 103 2.02E+3 4. 24E+3 5. 52E.5 1.61 E+4 6.79E+2 Ru- 105 1. 22E-0 B. 99E-1 1. 57E.4 4.84E6. 4.-E- 1 Ru- 106 B. 68E4 1.07E-5 1. 16E67 1. 64E.5 1.09E+4 Rh-103m Rh- 106 Ax- 11.o 9. 9BE3 7. 22E.3 1.09E.4 3. 67E+6 3. 30E.4 5.0OE*3 Sb- 124 3. 79E64 5. 56E.2 1.016E2 2.65E+6 5. 91E.4 1 .20E.4 Sb- 125 5. 17E.4 4. 77E.2 6.23E61 1. 646E6 1.47E-4 1.09E+4 Te- 125. 4. 76E.3 1. 99E.3 1.62E.3 4.47E+S 1.29E+4 6. 5BE.2 Te-127m 1. 67E-4 6. 90E.3 1..87 E 3 3. 756E4 1. 31E.6 2. 73E.4 2.07 E63 Te- 127 2. 23E.O 9.53E-1 1.85E+0 4. 86E6O 1.03E-4 2.44E.4 4.89E-1 Te-I29m 1. 41E-4 6. 09E63 S. 47E-3 3. 186.4 1. 6BE+6 6.90E-4 2. 23E.3 Te- 129 7. 88E-2 3.47E-2 6.75E-2 1.7SE-1 3.OOE*3 2. 63E+4 1.BBE-2 Te- 131. 1. 07E+2 S. 50E+1 B. 93E.1 2.65E62 1.99E.5 1. 19E.5 3. 63E61 3

TeI-1 1 1. 74E-2 8. 22E-3 1. 5BE-2 3.99E-2 2.06E-3 8. 22L-3 5.0OE-3 Te-132 3. 72E.2 2. 37E.2 2.79E62 I .03E63 3. 40E+5 4.416.+4 1 . 76E.2 1-130 6. 36E-3 1. 39E64 1.60E-6 1.53E*4 1. 99E.3 5. 57E63 1-131 3. 79E.4/ 4.144E64 1. 48E+7 5. 186.4 1.06E.3 1. 96E÷'4 1-132 1. 69E+3 3. 54E63 1.69E-5 3. 95E-3 1. 90E.3 I .26E.3 1-133 1. 32E-4 1.92E-4 3.56L*6 2.24 E-4 2. 16E-3 S. 60E.3 FERMI 2 ODCM - TRM VOLUME II 7-26 Rev. 13 I

Table 7.0-4 Raipo, Inhalation Pathway Dose Factors - INFANT (Cont.)

3 (mrem/yr per .Ci/m )

muclid* 10oo Liver Thyroid Kidney Luns CI-L.i T. body 1-134 9.21E+2 1.BBE-3 4.45E4 2.09E-3 - 1.29E.3 6.65E+2 1-135 3.96E*3 7.60E-3 6.96E-5 8.47E.3 - 1.83E-3 2.77E-3 Cs-134 3.96E£S 7.03E.5 - 1.90E÷5 7.97E.4 1.33E-3 7.65E-4 Cs-136 4.83E-4 1.35E.5 - 5.664E÷4 1.E18E+4 1.43E-3 5.29E.4 Cz-137 5. 49E.5 6.12£E5 - 1.72E.5 7.13E.4 1.33E+3 4.SSE.4 Cs-138 5.oSE-2 7.81E+2 - 4.1OE+2 6.S4L+1 8.76E.2 3.98E#2 Ba-139 1.48E+O 9.84E-4 - 5.92E-4 5.95E.3 S.1OE÷4 4.30E-2 Ba-140 5.60E.4 5.60E1 - 1.34E+1 1.601+6 3.834&E 2.90E+3 Ba-141 1.57E-1 1.08E-4 - 6.50E-5 2.97E-3 4.75E-3 4.97E-3 BU-142 3.96E-2 3.30E-5 - 1.90E-5 1.55E-3 6.93L+2 1.96E-3 L.-1O S.05E+2 2.OE2 - - 1.68E.S A.&8E.4 5.15E-1 La-142 1.03E£O 3.77E-1 - - 8.22E+3 5.95E.4 9.04E-2 Ce-141 2.77E÷4 1.67E+4 - 5.25E+3 5.17E+5 2.16E+4 1.99E£3 Ce-143 2.93E+2 1.93E+2 - 5.64E+1 1.16E*5 4.97E+4 2.21E#1 Ce-144 3.19E+6 1.21E+6 - 5.38E£5 9.84E÷6 1.48E+5 1.76E+5 Pr-143 1.40E£4 5.24E-3 - 1.97E÷3 4.33E*S 3.72E.4 6.99E+2 Pr-144 4.79E-2 1.85E-2 - 6.72E-3 1.61E-3 4.28E+3 2.41E-3 Nd-147 7.94E.3 8.13E+3 - 3.15E.3 3.22E£5 3.12E+4 5.00E+2 W-187 1.30E+I 9.02E0 - - 3.96E-4 3.56E÷4 3.12E.0 Np-239 3.71E+2 3.32E-1 - 6.62E÷1 5.95E+4 2.49E+4 I.88E+I FERMI 2 ODCM - TRM VOLUME II 7-27 Rev. 13

Table 7.0-4 Raipo, Grass-Cow-Milk Pathway Dose Factors - ADULT (mrem/vr per #Ci/m 3 ) for H-3 and C-14 2

(m x mrem/yr per lCi/sec) for others Nucl ide Done Liver Thyroid Kidney Luns GI-LLI T. Body H-3 7.63E-2 7.63E.2 7. 63E.2 7. 63E.2 7.63E.2 7. 63E62 C- 14 3. 63E-5 7.26E6'4 7.26E.4 7.26E64 7.26L.4 7. 26E+4 7. 26E.4 Na-24 2. 54E-6 2. 54E+6 2. 54E+6 2. 54E-6 2. 546 6 2. 54E+6 2. 54E+6 P-32 I . 716Z- 10 1. o6E6.9 1. 92Z-9 6. 60E-8 Cr-S1 1. 71E.4 6. 30E+3 3.80E+4 7. 20E.6 2.86E-4 54 Mn- B.60E.6 2. 50E+6 2. 57E+7 1.60E+6 Mn-56 4.23E-3 S.38E-3 1. 35E-1 7.51E-4 Fe-5S 2. SIE57 I. 73E-7 9. 67.+6 9. 956-6 4 .04E.6 7.006+.7 Fe-59 2.9BE-7 I.956+7 2.33E+8 2. 68E+7 Co-57 1. 28E+6 3.25E-7 2. 13E+6 Co- 58 4. 72E+6 9. 576.7 1.06E.7 Co-60 I. 64E.7 3.08E*8 3. 62E+7 Ni-63 6. 73E-9 6. 66E-8 9. 736.7 2. 26E+8 Ni-65 3.70E-1 4. 8 16-2 1. 22E-0 2.19E-2 Cu-64 2.4 1E.4 6. 086.4 2. 05E.6 1.13E+4 Zn-65 1. 37E-9 4. 36E-9 2. 92E.9 2. 7 SE-9 1 976E9 Zn-69 Br-82 3. 726.7 3.25E67 Br-83 1.49E-I 1.03E-1 Br-NI.

Br-85 Rb-86 2. 59E+9 5. 11+8 1. 216E9 Rb-88 Rb-89 Sr-89 1 .4.5E+9 2. 33E.8 6. 16E+7 Sr -90 4.6BSE 10 1. 35E9 1. 15. 10 Sr-91 3. 13E-4 1. 49E-5 1.27E.3 Sr-92 4.89E- I 9.68CE0 2. 116-2 Y-90 7. 07E. I 7. 50.+5 1. 90E.0 Y-910 Y-91 8. 60E.3 4. 736.6 2. 30E62 Y-92 5. 42E-5 9. 49E-1 1. SBE-6 Y-93 2. 33E-I 7. 396.3 6.643E-3 Zr-95 9. 46E+2 3.03E.2 4. 766-2 9. 62E.5 2.05E#2 7

Zr-9 4. 26E-I B. 59E-2 1.306-1 2.66E-4 3. 93E-2 Nb-95 B. 25E.4 4.59E-4 4. 54E+4 2. 79E+8 2. 47E66 Nb-97 5.47E-9 0o-99 2.52E67 5.72E+7 5. 85E-7 4 .80E-6 Tc-99m 3. 256.0 9. 19E6O 1.406.2 4.506.0 5. 44E*3 1. 17.+2 To-t01 R.- 103 1. 02E*3 3. 89E.3 1.19E,5 4. 39E62 Ru- 105 8. 57E-4 1.116-2 5. 24E-I 3.38E-4 Ru- 106 2.04E.4 3.94E-4 1. 32E-6 2. 58E+3 Rh- 103.

Rh- 106 At- 1100 5. 83E-7 5. 39E67 1. 06£,B 2.20E-10 3.20E.7 Sb- 124 2.57E+7 4.86E- 5 6.24E64 2.00E-7 7. 316E8 1.02E67

2. 286E5 2.086.' 1 . 58. 2.25E-8 4.86E-6 5b-125 2. 04E+?

Te- 125- 1. 63E-7 5.90E.6 4.90E-6 6.63E67 6. 50E.7 2.18E.6 Te-127. 4. 58E-7 1.64E67 1. 17E67 1. 86E+8 1. 54E68 5. 58E.6

2. 16E.2 4. 98E.2 2. 746.3 5,3o6*4 1. 456E2 Te-127 6. 72E+2 Te-129m 6.04E+7 2.2SE.7 2. 08E6 7 2. 52E+g 3.04E48 9.57E-6 Te- 129 Te-131i 3.61ES 1.77E+5 2.80E.5 1.79E*6 1.7SE- 7 1.47E65 Te-131

1. 55E-6 1.716.'. 1.49E+7 7. 32E.7 T.-132 2. 39E*6 hl 1.656.+6 1-130 6.26E-5 1. 2bE,6 1.07E-8 1. 96E-6 I .08E6. 4. 96E+5 1-131 2. 96E-8 4.26E+8 1.39E-11 1 7. 27E-8 1. 12F.B 2. 636E8 1-132 1.64E-1 S.37E-I 1.53E-1 9 6.97E-I 8.22E-2 1.53E-1 1-133 3. 97E+6 6.90E.6 I .01E-9 1. 20E67 6. 20C-6 2.10OE*6 FERMI 2 ODCM - TRM VOLUME II 7-28 Rev. 13

Table 7.0-4 Raipo, Grass-Cow-Milk Pathway Dose Factors - ADULT (CONT.)

(mrem/yr per yCi/m 3 ) for H-3 and C-14 2

(m x mrem/yr per /-tCi/sec) for others

-u1lide None Liver Thyroid Kidney L~ung1 CI -LUZ T. Body 1-134 1-135 1. 39E+4 3. 63E+4 2. 40E+6 5.83E+4 6.10E+4 1.34E+4 Cs-134 5. 65E9 1.34E. 10 4. 35E+9 I. 44!E9 2.35E-8 1. 10E+10 C.-136 2. 61E+8 1.03E-9 5. 74E-8 7.87E.7 1.17E+8 7. 42E-8 Cf-137 7. 38E+9 1.0 1E 10 3.43E.9 1.14E-9 1.95E.8 6. 61E-9 Cs-138 Ba -139 4.70£-8 S. 34E-8 1.38E-9 Ba- 140 2.69E+7 3.38E-4 1.15E+4 1.93E+4 S. 54A..7 1. 76E+6 Ba-141 Ba- 142 L.i- O40 4.49E+O 2. 26E!0 1.66E+5 5.97E-i La- 142 3.03E-8 Ce-141 4.84E+3 3.27E.3 1. 52E+3 1.25E+7 3. 71E+2 Ce-143 4. 19E.1 3.09E-4 1. 36E+ I 1. 16E+6 3.421.0 Ce-144 3. SSE-5 1. 50E.5 B.87E+4 1.21E+8 1. 92E+4 Pr-143 1. 59E+2 6.37E.I 3. 68E+ 1 6.96E+5 7. 88E.0 Pr- 144 Nd-147 9. 42E+ I 1. 09E.2 6.37E÷I 5.23E.5 6. 52!+0 W-187 6. 56E+3 5.48E+3 1 .80E-6 1. 92E+ 3 Np-239 3. 66E+0 3.60E-I 1. 12E+O 7. 39EtJ 1.98E-i FERMI 20DCM - TRM VOLUME II 7-29 Rev. 13 1

Table 7.0-4 Raipo, Grass-Cow-Milk Pathway Dose Factors - TEENAGER (mrem/yr per JICi/m 3 ) for H-3 and C-14

( 2 (m x mrem/yr per j.Ci/sec) for others Nucl ide Bone Liver Thyroid Kidney Lung GX-LUI T. Body H-3 9. 94E.2 9. 94E+2 9. 94E-2 9.94E-2 9. 94E- 2 9. 94E+2 C-I1 6. 70E. 5 1 .34E-5 1. 34 E-5 1.34EL5 1. 34E+5 1.34E-5 1.34E-5 Na-24 4. 44E+6 4. 44E-6 4. 44E46 4. 44E+6 4.44E+6 4.44E*6 4.44E+6 P-32 3. 15E+10 1.95E.9 2.65E-9 1.22E-9 Cr-51 2. 78E4 1.10E+4 7. 13E.4 B. 40E+6 S.OOE4 Hn-54 1. 40E+7 4. 17E.6 2.87E-7 2. 7BE-6

?In-56 7. S1E-3 9. SOE-3 4. 94E-I 1. 33E-3 Fe- 55 4. 4 E.7 3. 16E.7 2. 00OE7 I.37E.7 7.36E-6 Fe- 59 5.20E-7 1. 21E+8 3. 82E-7 2.87E-B 4. 6BE+7 Co- 57 2. 25E,6 4. 19E.7 3. 76E+6

1. 83E+7 Co-SB 7. 95ES6 I . 10E-0 Co-60 2. 78E+7 3. 62E£B 6.26E+7 Ni-63 1. 18E+10 a. 35Z.8 1 . 33E88 4.01E+8 Ni-65 6. 7BE-1 8. 66E-2 4.70E+O 3.94E-2 4.29E-4 1,09E-S 2.02E÷4 Cu-64 1. 3M36 Zn-65 2. 11E÷9 7. 31E.9 4. 68E-9 3. 10÷.9 3. 4 1£ 9 Zn-69 Br-82 5. 64E÷7 Br-83 1.91E-1 Br-84 Br-85 Rb-86 4. 73E.9 7.OOE+8 2. 22E.9 Rb-88 Rb-89 sr-B9 2.67E+9 3. 1BE-8 7.66E-7 Sr-90 6.61E-10 1.B6E+9 1.63E 10 Sr-91 5.75£*4 2.61E-5 2. 29E+3

.Sr-92 B. 9SE-1 2.28E+1 3. 81E-2 y-90 1. 30E.2 1 .07E+6 3. 50E0 Y-91.

Y-91 1. SBE-4 6. 4BE 6 4.24E>2 Y-92 1.OOE-4 2. 75E0 2.90E-6 Y-93 4. 30E-1 1.E31.4 1. MS-2 Zr-95 1. 65E,3 5. 22E+2 7. 67E+2 1.20E5£6 3. 59E-2 Zr-97 7. 7SE-1 1. 53E-1 2. 32E-1 4. 15E..4 7.06E-2 Hb-95 1. 41E+5 7.801+4 7.57E+4 - 3.34E#8 4. 30E-4 Hb-97 - 6.34E-8 Ilo-99 4. 56E+7 1.04AE+ - B.16E+7 B.69E+6 Tc-99a S. 64E+0 1. 57E1 2.34E,2 8.73E+0 1.03E+4 2.04E+2 Tc-101 Ru-103 1.81E-3 6.40E+3 - 1.52£:.5 7.75E-2 Ru- 105 1. 57E-3 1. 97E-2 1.26EO 6. ME-4 Ru- 106 3. 75E£4 7. 23E.4 1.80E+6 4. 73E.3 Rh- 103.

Rh- 106 AS- 110. 9. 63E47 9.1 11.7 1. 74E-8 2.56E-10 5. S4E-7 Sb-124 4. 59E.7 8.46E+5 1.04E+5 4.01E-7 9.25E.8 1. 79E-7 Sb-125 3.65E-7 3.99E,5 3.49E,4 3.21E-7 2.84E+8 8.54E-6 25 1.08E-7 Te-t m 3.OOE-7 S. 39E-6 - 8.86E-7 4.02E+6 Te-127m 8.44E+7 2.99E-7 2.01E.7 3.42E-8 - 2.10E-8 1.00E>7 le-127 1. 24E-3 4.41E+2 8. 59E-2 5. 04E,3 - 9.61E-4 2. 6SE, 2 29 Te-1 . 1. IE.8 4. 10E-7 3.57E+7 4. 62E.8 - 4.15E+B 1.75E4 7 9

Te-12 1.67E-9 - 2.18E-9 Tt-131m 6. 57E.5 3. IS£5 '.74£÷5 3.29E-6 - 2.53E+7 2. 63E-S Te-131 Te-132 4. 28E-6 2.71E-6 2.86E-6 2.60E+7 B.SBE-7 2. 55E-6 1-130 7.49E-5 2.17E.6 1.77E-8 3.34E-6 1.67E-6 B.66E-5 1-131 S. 3SE*8 7.53E-8 2.20E-11 1. 30E-9 1.49E*8 4.04E.B 1-132 2.90E-1 7.59E-1 2.56E41 1. 20C-D 3.31E-1 2. 72E-1 1-133 7. 24E-6 1.23E+7 1.72E-9 2. 15E 7 9.30E*6 3. 75E-6 FERMI 2 ODCM - TRM VOLUME I! 7-30 Rev. 13

Table 7.0-4 Raipo, Grass-Cow Milk-Pathway Dose Factors - TEENAGER (Cont.)

3 (mrem/yr per UCi/m ) for H-3 and C-14 2

(m x mrem/vr per LCi/sec) for others Huclide &one Liver Thyroid Kidney Luna Ql-1. T.Iod6y 1-136 1-135 2.47E.4 6. 3 5E4 4.08E.6 1.00E+5 7.03£E4 2. 351.4 C.- 134 9. 81E.9 2. 31E-10 7. 34E-. 2.80E.9 2. 97E+8 1.07E-10 Cs-136 4. 45E.8 1.75E-9 9. 53E-8 1. 50E.8 1.411+8 1. 18.+9 Ca- 137 1.34E. 10 1. 78E.10 6.06E.9 2. 35E.9 2. 53E.8 6,20E.9 Cs-138 A.-139 S. 69E-8 7.75E-7 2. 53E-9 Ba-140 4.8 5E÷7 S. 95E-4 2.02E+4 4.OE"-4 7.49E.7 3. 13E+6 Ba-141 R.- 142 La- 140 8.06E-0 3. 96E+0 2.27E+5 1.05£.0 La- 142 2.23E-7 Ce-141 3. 87£.3 5. 92E.3 2. 79F.3 1. 69E+7 6. 81+2 Ce- 143 7.69E.1 5. 60E.4 2. 51£.1 1. 681E6 6. 25E.0 Ce-144 6. 58E+5 2. 72E.5 1. 63E.5 1 . 66E1. 3. 54E-4 Pr-143 2. 92E.2 1. 17E+2 6.77E+1 9.61 E÷5 1.45E+1 Pr-144 Nd-147 1 .81E+2 1. 97E+2 1. 16E+2 7.1 1E+5 1.18E+1 W-187 1. 20E.4 9. 78E.3 2.65E16 3.43E+3 Np-239 6.99E+0 S. 59E-I 2.07E+0 1.061.5 3.66E-1 FERMI 2 ODCM - TRM VOLUME II 7-31 Rev. 13

Table 7.0-4 Raipo, Grass-Cow-Milk Pathway Dose Factors - CHILD 3

(mrem/yr per yCilm ) for H-3 and C-14 2

(m x mrem/yr per UCi/sec) for others Nuclide Bone Liver Thyroid Kidney Luns GI-LLI T.Body N-3 - 1.5?E.3 1.57E.3 1.SM-3 i.57E-3 1.57E.3 1.57£.3 c-14 1.65E+6 3.29E.5 1.29E-5 3.29E*5 3.29E-5 3.29E!5 3.29E.5 Na-2. 9.23E-6 9.23E÷6 9.23E+6 9.23E+6 9.23E+6 9.23E.6 9.23E+6 P-32 7.77E+10 3.64E+9 - - 2.15.E9 3.OOE+9 Cr-51 - - 5.66E-4 1.55E.4 1.03E-5 5.41E÷& 1.02E+S Mn-54 - 2.09E.7 5.8E.6 - 1.76E+7 5.58E-6 Mn-56 - 1.31E-2 1.58-2 - 1.90E-O 2.95E-3 Fe-55 1.12E+8 5.93E7 - - 3.35E-7 1.10E.7 1.84E.7 Fe-59 1.20E*8 1.95E.8 - 5.65E+7 2.03E-8 9.71E+7 Co-57 - 3.84E+6 - - 3.14E?7 7.77E+6 Co-58 - 1.21E.7 - - - 7.08E-7 3.72E.7 Co-60 - 4.32E-7 - - - 2.39E*8 1.27?t8 Ni-63 2.96E.10 1.59E+9 - - 1.O7E.8 1.01E+9 Ni-65 1.66Z.0 1.56E-1 - - - 1.91E.1 9.11E-2 Cu-b4 - 7.55L+4 - 1.82E.5 - 3.54E-6 4.56E.4 Zn-65 4.13E-9 1.10E-10 - 6.94E.9 - 1.93E-9 6.85E+9 Zn-69 - 2.14E-9 -

Br-82 - 1.1SE+8 Br-B3 - - 4.69E-1 Br-84 - -

Br-85 - -

Rb-86 - 8.77E.9 5.64E+8 5.39E*9 Rb-88 - -

Rb-89 - - -

sr-89 6.62E+9 - 2.56E.8 1.89E.8 Sr-90 1.12÷11 - 1.51iE.9 2,83E+10 Sr-91 1.41!i5 - - 3.12E#S 5.33E+3 Sr-92 2.19E+0 - - 4.14E.I 8.76L-2 Y-90 3.22E+2 - 9,5E+5

.- 8.61E+O Y-91m -

Y-91 3.91E+4 - 5.21E+6 1.04E+3 Y-92 2.46E-4 - 7.10E+0 7.03E-6 Y-93 1.06E+0 - 1.57E.4 2.90E-2 Zr-95 3.84E.3 8.45E+2 1.21E+3 - 8B1E+S 7.52E+2 Zr-97 1.89E-0 2.72E-1 3.91-1 - 4.13E+4 1.61E-I Nb-95 3.18E+5 1.24ES 1.16E+5 - 2.29E+8 8.84E+4 Nb-97 - - 1.45E-6 -

mo-99 - 9.29E*7 1.77E.8 - 6.86E+7 2.05E+7 99 Tc- m 1.29E-1 2.54E£1 3.68E,2 1.29E+1 1.441.4 4.20E+2 Tc-101 - -

Ru-103 4.29E+3 - 1.08E.4 - 1.11E+5 1.65E!3 Ru-105 3.82E-3 - 3.36E-2 - 2.49E+0 1.39E-3 Ru-106 9.24E.4 - 1.25E-5 - 1.44E+6 1.15!+4 Rh-l03m - -

Rh-106 - -

AZ-110m 2.09E+8 1.41E+8 2.63E+8 1.68E+I0 1.13E+8 Sb-12A 1.09E-8 1.41E-6 2.40E÷S - 6.03E-7 6.79E+8 3.81!.7 Sb-125 8.70E.7 1.415+6 8.06E-' - 4.85E.7 2.08E-8 1.82!.7 Te-125a 7.38E.7 2.0O!+7 2.07E+7 - - 7.12E+7 9.84E+6 Te-127. 2.08E.8 5.60E.7 4.97E?7 5.93E.8 - 1.68E+8 2.47E?7 Te-127 3.06!+3 8.25E+2 2.12E+3 8.71E.3 - 1.20E-5 6.56E.2 Te-129m 2.72E÷8 7.61!.7 8.78!+7 8.00E+8 - 3.32£+8 4.23E+7 Te-129 - 2.87E-9 - 6.12E-8 -

Te-131- 1.60E!6 5,53E+5 1.1i.56 5.35E.6 2.24!.7 5.89E*5 Te-131 Te-132 1.02E!? 4.52E-6 6.58E+6 4.20!.7 4.55?+7 5.46!.6 1-130 1.75E+6 3.54!.6 3.90E+8 5.29E-6 1.66E+6 1.82E.6 1-131 i.30£÷9 1.31E-9 4.34£E11 2.ISE.9 1.17E+8 7.46E4B 1-132 6.86E-I 1.26E.0 5.85E+1 1.93E+O 1.48E+O 5.80E-I 1-133 1.76!.7 2.18E.7 4.04E.9 3.63!.7 8.77E.6 8.23E.6 FERMI 2 ODCM -TRM VOLUME II 7-32 Rev. 13

Table 7.0-4 Rai p o, Grass-Cow-Milk Pathway Dose Factors - CHILD (CONT.)

(mrem/yr per UCi/m 3 ) for H-3 and C-14 (m2 x mrem/yr per 9Ci/sec) for others mucilde sooe Liver Thyroid Kidney LAng GCI-LUI T.body 1-134 1-135 5.84E*4 1.05-S5 9.30E6 1.61E .5 2.00E+8 4.971.1.

Ca-134 2.26SE10 3.71E.10 - I.15E.10 4.13E.9 7.83E*9 Cs-136 1.00E-9 2.76E+9 - 1.47E-9 2.19E.8 9.70.-7 1.79E.9 Cs-137 3.22E.10 3.09E+10 - 1.01E-10 3.62E-9 1. 93E.8 4. 55E-9 Cz-138 9

Ba-13 2. 14E-7 1. 23E-5 6. 19E-9 Ba- 140 1. 17E+8 1.03E+5 3. 34E+4 6.121-4 5.994E.7 6.841.6 Ba-141 2

BA-14 LA- 140 1. 93E+1 6.74E£0 1. 88&. 5 2.27E÷0 La-142 2.5 1E-6 CU-141 2. 19E+4 1.09E+4 4. 78E13 1. 36E+7 1.62E+3 Ce-163 1.89E+2 1.02E+5 4.29E+1 1. 50E.6 1.481.1 Ce-144 1.62E+6 5.09E-5 2.82E+5 1. 33E+8 8.66E+4 Pr-143 7. 23E+2 2.17E+2 1. 17E+2 7. 80gt 5 3. 59E. 1 4

Pr-1 4 Nd-W14 4.4A£÷2 3.60E+2 1. 98E.2 5. 7 1E.5 2. 79E÷1.

W- 187 2.91E÷4 1. 72E-4 2. 42E.6 7. 73E13 Np-239 1. 72E-1 I .23E-0 3.57E+0 9. 14E+4 8.68E--1 FERMI 2 ODCM - TRM VOLUME I! 7-33 Rev. 13 1

Table 7.0-4 Raipo, Grass-Cow-Milk Pathway Dose Factors - INFANT 3

(mrem/yr per uCi/m ) for H-3 and C-14 2

(m x mrem/yr per jUCi/sec) for others Nuclide Bone Liver Thyroid Kidney Lun* GI-LII T. Body H-3 2. 3SE-3 2.38E-3 2.382E3 2. 38E.3 2.38E+3 C-14 3.23E-6 6. 89E+5 6. 89E-5 6. 892.5 6.892+5 6.89E÷5 6.89E+5 Na-24 1.61E-7 1. 61E.7 1.6 I£7 1.61E+7 1. 61E-7 1.61E.7 1. 61E+7 P-32 1. 60E- 11 9. 42E.9 2. 17E-9 6. 21E-9 Cr-51 I .0 S 85 2. 30E+4 2.05E+5 4.71+6 1. 61E+5 Mn-S4 - 3.89E.7 - 8.63E.6 1.43E.7 8. 83E+6 mn-56 - 3.21E-2 - 2. 76E-2 2.91E-0 5. 53E-3 Fe-55 1.35E-8 8.72E.7 - 4.27E÷7 1.112-? 2. 33E+7 Fe-59 2.25E8B 3.93E.8 - 1. 16E+8 1.88E-8 1. 552.8 Co-57 - 8.95+6 - 3.05ES7 Co-S$ - 2.43E+7 - 6.05E+7 6.06E+7 Co-60 - 8.81E.7 - 2. 10E-8 2. 08L+8 NI-63 3.49E,10 2.16E÷9 - 1.07E.8 1. 21E+9 Ni-65 3.51E£0 3.97E-I - 3.02E-1 1 .81E-1 Cu-64 - 1.88+5 - 3. 17E.5 3. 85£-6 8. 69E.4 Zn-65 5.55E89 1.90E-10 - 9.23E+9 1. 61E+10 8. 782E9 Zn-69 - - - 7. 36E-9 Br-82 - - - 1. 94E-8 Br-83 - - - 9.958-I Br-84 - - -

Br-8S - - -

Rb-86 - 2.22E+lo - 5.69E*8 1.10E2.0 Rb-88 - - -

Rb-89 - - -

1.26E+10 - - 2.$92,8 3.61E+8 Sr-89 Sr-90 1.22E-11 - - 1. 52E+9 3. 10EI10 Sr-91 2.9/.E.S - - 3.49E#5 1. 06E24 Sr-92 4.65E+O - - 5.0 1£.i 1. 73E-I Y-90 6.80L£2 - - 9. 392.5 1. 82E- I Y-91m Y-91 7.33E-4 - - 5. 26E.6 1. 95E+3 Y-92 5.22L-4 - - 9. 972.0 1.47E-5 Y-93 2.25E+0 - - 1.78E-4 6.13E-2 Zr-95 6.83E+3 1.66E.3 - 1. 79E-3 8. 288.5 1. 18E+3 Zr-97 3.99E+O 6.SS-1 - 6.91E-I 4. 372.4 3. 13E-I Nb-95 5.93E+5 2.44E.5 - 1. 752.5 2. 06E.8 1. 41£+5 Wb-97 - 3. 70E-6 Mo-99 - 2.12E.8 - 3. 172+8 6. 98E+7 4. 13E+7 Tc-99m 2.69E+I 5.5SE+1 - 5. 97E+2 2.90E+1 1.61E.4 7. 15.+2 Tc-lO1 -

Ru-103 8.69E+3 - 1.812.4 1.06E-5 2. 91E.3 Ru-lO5 8.06E-3 - 5. 92E-2 3. 21E80 2. 71E-3 1.90E.5 - 2. 252.5 1. 44E-6 2. 38E+4 Ru-106 Rh-103m - -

Rh-106 - -

3.86E+8 2.82E-8 4.03E-8 1. 46E+10 1.86E+8 A4-110m

1. 331E-8 6. 46E.8 6. 49E÷7 Sb-124 2.09E-8 3.08E.6 5.56E-5 Sb-125 1.49E.8 1.45E.6 1.87E.5 9. 38E+7 I. 99E.8 3.07ELi7 Te-iZSm 1.58iE8 5.04E.7 5.07E-7 7. 182.7 2.04E-7 1.22E.8 1.04E-9 1.70E-8 S. 10E7 Te-127m 4.218E8 1.40E*8

1. 59E-4 1. 362.5 1. 40E-3 Te-127 6.50E£3 2.18E-3 5.29E*3 Te-129. 5.59E*8 1.92E+8 2.15E+8 1. 40E-9 3. ý3E48 8.62E-7 Te-129 2.08E-9 - 1.751-9 5. 182-9 1. 66E-7

9. 35E26 2. 29E.7 1. 12E+6 Te-131m 3.38E-6 1.36E.6 2.7bE.6 Te-131 6.51E-7 3. 85E. 7 9. 72E.6 Te-132 2.10E2? 1.04E27 1.54E.7

8. 70E26 1. 70E+6 3. 88E26 1-130 3.60E-6 7.92E26 8.682+8 2.72E-9 3.21E.9 1.05E-12 3. 75E.9 1. 15.8 1.41E-9 1-131

3. 22E.0 2. 34E-0 1.032.0 1-132 1.42E-0 2.89E.0 1.35E-2

6. 36E.7 9. 16.-6 i. S8£.7 1-133 3.72E-7 5.41E.7 9.84E-9 FERMI 2 ODCM - TRM VOLUME II 7- 34 Rev. 13

Table 7.0-4 Raipo, Grass-Cow-Milk Pathway Dose Factors - INFANT (CONT.)

(mrem/yr per UCi/m 3 ) for H-3 and C-14 (m 2 x mrem/yr per .Ci/sec) for others IuO ide boat Liver Thyroid Kidney Lung G1-LLX T. body 1-134 1.0WE-9 1-135 1.21E+S 2.41E÷5 2. 16E-7 2.69E+5 8.74E+4 8. 80K-4 Cx- 134 3,65E£10 6.80E+10 1.75E+10 7. 18E+9 1. 8 5E+8 6. 87E÷9 Cs-136 1.96E+9 5.77E+9 2.30E*9 6. 70E+8 8.76E+7 2. 1SE÷9 Cs-137 5.15E.10 6.02E-10 1. 62E÷ 10 6. 55E+9 1. 88E-8 4. 27E-9 Cs-138 Ba-139 4.55E-7 - 2.88K-5 1. 32E-8 8.- 140 2.4iE÷8 2.41E.5 5.73E-4 1.48.*5 5.92E+7 1. 24E7.

8a-141 As-142 La- 140 4. 03E- 1 1. 59E-1 1.87E-5 4.09E.O 1a- 142 5.21E-6 Ce-!41 4. 33E.4 2. 64.4 - 8.15E.3 - 1.37E+7 3.11E*3 Ce-143 4. DOE+2 2. 65K.5 - 7.72E.1 - 1. 55E6 3. 02E. 1 Ce-144 2. 33E+6 9. 52E+5 - 3.85E+5 - 1. 33E-8 1. 30E-5 Pr-143 1. 49E-3 5. 59E.2 2.08E+2 7. 89E*5 7. 41E.1 Pr-144 Nd-147 8. 82E+2 9. 06E-2 3.49E+2 5.74E-5 5. 55E+1 W-187 6. 12E-4 4.26E-4 2. 50E+6 1. 47E+4 Np-239 3. 64E+I 3. 25E.0 - 6.49E+0 9.40E+4 1.84E.0 FERMI 2 ODCM - TRM VOLUME I1 7-35 Rev. 13 1

Table 7.0-4 Raipo, Grass-Cow-Meat Pathway Dose Factors - ADULT 3

(mrem/yr per U Ci/m ) for H-3 and C-14 2

(m x mrem/yr per UiCi/sec) for others Nucl ide Bone Liver Thyroid Kidney Lu rs GI-LLI T. Body H-3 3.25E2 3. 25E+2 3. 25E£2 3. 25E. 2 3. 25E.2 3.25E+2 C- 14 3. 33E-5 6.66E.4 6. 66E£4 6. 66E-4 6.66E.4 6.66£E4 6. 661.4 Na-2V 1. 84E-3 i. 84 E-3 1.84E-3 1. 84£-3 1. 84E-3 1. 84E-3 1.E-3 P-32 4.65E49 2.89E+B S. 23E+8 Cr-SI 4. 22E- 3 1. 56£+3 9. 38E- 3 1.78E-6 7. 07E+3 Hn-54 9. 15E+6 2.72£E6 2. 80CE 7 1. 75E+6 mn-56 Fe-55 2. 93E-8 2.02E-8 1. 13E÷8 1. 16E-8 4.72£.7 Fe-S 9 2. 67E£8 6.27£+B 1. 75E+8 2.09E+9 2. 40E+8 Co-57 5.64E-6 1. 43E+B 9. 37E£6 Co-58 1.83£,7 3. 70E-8 4. 10.E+7 Co-60 7. 52£.7 1 .4 1E+9 1. 66E+8 Ni-63 1.89E.10 1. 31E+9 2. 73E-8 6. 33E+8 Ni-65 Cu-6' 2.95E-7 7.45E-7 2. 52£-5 I.39E-7 Zn-65 3. 56E-8 1. 13£E9 7. 57E+8 7. 13E+8 S.12E.8 Zn-69 Br-82 I .44E-3 1. 26E+3

-r-83 Br-84 Or-S5 Rb-86 4. B8E-8 9.60E£7 2. 27E.8 Rb-88 Rb-89 Sr-89 3.01E£8 4.86 E.7 8. 65E-6 Sr-90 1.24E. 10 3. 59£÷8 3.05E+9 Sr-91 1.3BE-9 Sr-92 Y-90 1.07£E2 1. 13E+6 2.86E+0 Y-91g Y-91 1. 13E+6 6.24E+8 3.03E'4 Y-92 Y-93 2.08£-7 Zr-95 1.98E+6 6.04E.5 9.48EB5 1. 91E+9 409E45S Zr-97 1.83E-5 3. 69E-6 5. 58E-6 1.141E+O 1.69E-6 Nb-95 2. 29E+6 1.28£E6 I.26E-6 7.75E+9 6.86E£5 Nb-97 No-99 1 .09E45 2.46E£ 5 2. 52E£5 2.07£E4 Tc-99.

Tc-101 Ru- 103 1.06E-B 4.03E-8 1.23£E10 4. 5SE.7 Ru- 105 Ru-106 2.8OE-9 5. 40E+9 1.81 E-11 3. 54E+8 Rh- 103.

Rh- 106 A4-1 100 6. 69E.6 6. 19E-6 1.22£.7 2. 52E+9 3.67E+6 Sb- 124 1. 98E.7 3.74E. 5 4. 80£.'. 1.541E+7 S. 62E+8 7. 85E+6 Sb-125 1. 911E.7 2. 13E-5 1. 94E.4 1.47E+7 2. 10£.8 4. 54E+6 Te-125m 3. 59E+8 1. 30E+8 1.08E-8 1. 46E.9 1.43E÷9 4.81£.7 Te-12?m 1. 12E+9 3. 99E-8 2.8 5£.8 4.53E-9 3.74E+9 1. 36E*8 Te-127 1.09E-9 2. 10E-Z Te- 129. 1. 14E4 9 4. 27E-8 3. 93E-8 4. 77E-9 5. 76E-9 1.8 E-8 Te-129 Te-131. 4. 51E,2 2. 21E-2 3. 50E-2 2. 24E3 2. 19E-4 1. 84E-2 Te-131 Te-132 1.40£E6 9.07E-S 1 .OOE.6 B. 73E+6 4.29E+7 8.51E-5 1-130 2. 35£-b 6. 94E-6 5. 88£- 1.08E-S S.CSS£.9 5. 98£-6 2.74E-6 1-131 1.08£+7 1. 54£+7 5.05£-9 2.664E+7 4.07E.6 8.83E+6 1-132 1-133 4. 30E-I 7.47£-1 1. 10E-2 1. 30E.0 6.72E-i 2.2kE-I FERMI 2 ODCM - TRM VOLUME II 7-36 Rev. 13

Table 7.0-4 Raipo, Grass-Cow-Meat Pathway Dose Factors - ADULT (CONT)

(mrem/yr per /.LCi/m 3 ) for H-3 and C-14 (m 2 x mrem/yr per )iCi/sec) for others Liver Thyroid Kidney Lung CI-LLI ..body 1-134 1-135 CR- 134 6. 57E-8 1. 56E+9 5.06E*8 1.68E÷8 2.7 74E 1.28E+9 Cs- 136 1. 186.7 6. 67.+7 2.60£*7 3.56E+6 S. 30.E6 3.36£E7 Cs-137 8. 72E*8 1. 19E+9 4. 05£ 8 1. 35E+8 2. 31E.7 7.81E.8 Cs-138 go-139 Bar- 140 2. 88?7 3. 61E+4 i.23E-4 2.07E+4 5.92L.7 1. 89E+6 Ba- t4 Ba-142 L4-140 3.60E-2 1.81E-2 1. 33E.3 4.79E-3 La- 142 Ce- 14 1 1.406.4 9. 48E.3 4.40E+3 3.62E.7 1.086+3 Ce-i43 2.09E-2 1. 556+ I 6.806-3 5. 78E+2 1.71E-3 Ce-144 1. 46E+6 6. 09E.5 3.61E+5 4.93E+8 7.83E64 Pr-143 2. 13E+4 8. 54E.3 4.93E+3 9. 336.7 1. 06E+3 Pr-164 Nd-147 7.OaE÷3 B. 18E+3 4. 78E+3 3.93E.7 4. 90E-2 W-187 2. 16E-2 1.81E-2 5.92t*0 6. 32E-3 Np-239 2. 56E-1 2. 51E-2 7.84E-2 5. 15E+3 1.39E-2 FERMI 2 ODCM - TRM VOLUME II 7-37 Rev. 13

Table 7.0-4 Raipo, Grass-Cow-Meat Pathway Dose Factors - TEENAGER 3

(mrem/yr per /LCi/m ) for H-3 and C-14 2

(m x mrem/yr per uCi/sec) for others Nuclide Bone Liver Thyroid Kidney Lung I-LLI T. Body H-3 1. 94E+2 1. 94E*2 1.94E+2 1 . 94E12 1.94E+2 1. 94E.2 C-14 2. 81E5 5.62E.4 5. 62E4 5. 62E+4 5.62E+4 S.62E+4 5.62E.4 Na-224 1.47E-3 1. 4 7E-3 1. 47E-3 1.47E-3 1.47E-3 1. 47E-3 1.47E-3 P-32 3. 93E.9 2.44E.5 3. 30E+8 1.52E+8

3. 14E.3 1. 24E3 8.07E13 9. 5OE.5 5. 65K.3 Cr-S1 Mn-54 6.98E*6 2.O8E+6 1. 431+7 1. 38E.6 6

Mn-5

2. 38E-8 1.69E-8 1 .07E8 7. 30E7 3. 93E.7 Fe-55

2. 13E£8 4.98E+B 1. 57E+g 1. 92,85 Fe-59 Co-57 4.53E-6 8. 4SE-7 7. 59E.6 Co-58 1.41£÷7 1. 94E18 3.25K.7 Co-60 5. 83E+7 7.60E+8 1. 31E.8 Ni-63 1. 52E+10 1.07E+9 1. 71 E48 5. 151.8 Ni-65 Cu-64 2.4 1K-7 6. 10E-7 1.57E-5 1. 13£-7 Zn-65 2. S0E8 8. 69E+5 S. 56E+8 3.68E-8 4. 051.8 Zn-69

9. 98E+2 Br-52 Br-83 Br-84 Br-S5 Rb-86 4.06E18 6.01E.7 1. 91E.8 Rb-88 Rb-89 Sr-89 2. 54ký.. 3. 03E÷7 7.291+6 Sr-90 8.05E+9 2. 26E.5 1. 991+9 Sr-91 I. 10E-9 Sr-92 Y-90 S. 98S+ 1 7. 40E÷5 2.42E+0 Y-91.

Y-91 9.56E+5 3.92E+8 2. 56E+4 Y-92 Y-93 1.69E-7 Zr-95 1.518E6 4.76E+5 6. 991.5 1. 101E9 3. 27E# S 7 8. 15E-1 1. 39E-6 Zr-9 1. 53E-5 3.02E-6 4. SS-6 Nb-95 1. 79E+6 9.94E*.5 9. 641+5 4.25E-9 5. 47£+S Nb-97 mo-99 S. 98£÷4 2.06E+5 1.611,5 1. 71L.4 Tc-99m Tc-101 Ru-103 8. 60E-7 3. 03E.8 7. 1S1-9 3.68E+7 Ru-105 Ru- 106 2. 36E+9 4. 55E+9 1. 13E.11 2.97E.8 Rh-103m Rh- 106 A.s- 110O 5. 06E-6 4. 79E-6 9. 14E16 1. 351.9 2. 91E.6 Sb-124 i.62Z+7 2. 99E.5 3.67 E-4 1.41E.7 3.26E-8 6. 31£.6 Sb-125 1. 56E.7 i .71E.5 1.49E.4 1. 37E÷7 1. 22E.8 3. 66E.6 Te-125m 3.03E-8 1.091.5 8.47E-7 B. 94E+. 4.05E÷7 Te-127m 9. 41E.8 3. 34E.S 2.24EK8 3. 82E+9 2. 35E-9 1. 121+8 Te-127 1. 75E-8 Te-129. 9. S8£*S 3. 561+. 3.09E.8 4. 01E.9 3. 60.9 1. 52E-8 Te-129 Te-131m 3. 76E+2 i .80E.2 2. 71E.2 1.88E-3 1. 45E+4 1 . 50K.2 Te-131 Te-132 1. 15E-6 7. 26E. 5 7.661.5 6.197E16 2. 30E+7 6. 84E-5 1-130 1.89E-6 5.48E-6 4,47E-4 S. 44E-6 4. 21E-6 2. 19-6 1-131 8. 95E.6 1. 25.E7 3.66E-9 2.16K.7 2. 48E+6 6. 73E-6 1-132 1-133 3. 59E- I 6. 10E-I S. 51£+1 1.07E-0 4.61E-1 1. 86E- I Rev. 13 7-38 FERMI 2 ODCM - TRM VOLUME I1

Table 7.0-4 Raipo, Grass-Cow-Meat Pathway Dose Factors - TEENAGER (CONT.)

I (mrem/yr per U1Ci/m 3 ) for H-3 and C-14 (m 2 x mrem/yr per yCi/sec) for others Nuclide bobe Liver Thyroid Kidney Lunrk CI-LLI T. body 1-134 1-135 Cs-134 5. 23E.8 1.23E.9 3. 911.8 1.491+8 1.53E+7 5.71E+8 CS-136 9. 221E6 3. 63E-7 1. 97E+7 3. 111.6 2.92E+6 2. 44E.7 Cs-137 7. 24E+8 9. 63E18 3. 281+8 1.27E-8 I. 37E17 3. 36E+8 Ca-138 8a-139 Ba- 140 2. 38E.7 2. 91E.4 - 9.88E+3 1.961.4 3.67E+7 1.53E+6 Ba- 14 1 Ba- 14 2 La-140 2. 96E-2 1.45E-2 - - 8.351.2 3.87E-3 La- 142 Ce-141 1. 18E.4 7.86£*3 - 3.70E+3 - 2.25L.7 9.01Z#2 Cc-143 1. 76E-2 1 .28E.1 - 5.74E-3 - 3.85E+2 1.43E-3 Ce- 141. 1.23E.6 5.08E÷5 3.04E+5 - 3.09E+8 6.60E.4 Pr-143 1.79E1. 7. 151E3 4.16E+3 5.90E.7 8.92E+2 Pr-144 Nd-147 6. 241E3 6. 79E13 3.98E+3 - 2.45E+7 4.06E+2 W-187 1.81E-2 1.481-2 - 3,99E+0 5.17E-3 Np-239 2.23E-1 2. 11E-2 6.61E-2 - 3.39E-3 1.17E-2 FERMI 2 0DCM - TRM VOLUME II 7-39 Rev. 13 1

Table 7.0-4 Raipo, Grass-Cow-Meat Pathway Dose Factors - CHILD (mrem/yr per uCi/m 3 ) for H-3 and C-14 2

(m x mrern/yr per /LCi/sec) for others Nucl ide Bone Liver Thyroid Kidney Lung GI-LLI 7,Body H-3 2. 346.2 2.34E+2 2.34E-2 2.34E-2 2. 316.2 2. 34E62 C-1i. 5.29E+5 1.06E+5 1.06£.S I. 06E# 5 1.06E+5 1. 06£.5 1.06E-5 Na-24 2. 34E-3 2.34£-3 2.34E-3 2.34E-3 2.34E-3 2. 346-3 2. 34E-3 P-32 7. 41E-9 3. 476.8 2. 05E+8 2. 86E*8 4.89E+3 1. 346-3 8.93E+3 Cr-51 4.67E-5 8.81E63 mn-S4 7. 99E-6 2. 246.6 6.70E÷6 2.13E+6 mn-56 Fe-55 4. 57E.8 2.426.8 1. 37E68 4. A91.7 7.51.?7 Fe-59 3. 7BE-B 6. 12£-8 1.77E68 6. 37£.8 3.05£-8 Co-57 5.92£-6 4.85£E7 1.20£?7 Co-58 1.65E£7 9.60E-7 5.04£.?

Co-60 6.93E£7 3. 84E-8 2.066-8 Ni-63 2. 91E. 10 1. S6£-9 1.056-8 9.91E-8 Ni-65 Cu-64 3.24E-7 7.82£-7 1.52£-5 1.96£-7 Zn-6S 3.7 SE-8 1.00E9 6. 30E-8 1. 766.8 6. 226*8 Zn-69 Br-B2 1.56E-3 3

Br-8 4

Br-8 Br-85 Rb-86 5.76E-8 3.71£.7 3. 54E.8 Rb-88 Rb-89 Sr-89 4. 82E.8 I.86£-7 1.386.7 Sr-90 1.04E. 10 1. 40E÷8 2.64E-9 Sr-91 1. 016-9 Sr-92 Y-90 1.70E.2 4.84E.5 4.556+O Y-91m Y-91 1.81E-6 2.416E8 4.83E-4 Y-92 Y-93 1.55E-7 Zr-95 2. 68E+6 5.89£-5 8.43E65 6.146*8 5.24E-5 Zr-97 2. 84E-5 4.10£-6 5.89£-6 6.21£-I 2.42E-6 Nb-9s 3.09E-6 1. 20E.6 1.13E+6 2. 236*9 8.61£-5 Nb-97 No-99 1. 25E÷S 2.67?*5 1. 03E+5 3.096-4 Tc-99u Tc-101 Ru-103 1. 56E+8 3. 926.8 4. S.98E÷7 Ru- 105 Ru-lO6 4.44.9 S.996+9 6. 90E. 10 5. 546.8 Rh-103m Rh-106 AS- 11 O 8.40E-6 5.67E-6 1.06E-7 6.756*8 4.53E+6 Sb-124 2.93E£7 3. 80E. 5 6. 46E64 1.62E.7 1.83E-8 1.03£.7 Sb- 125 2.85£E7 2.19E+5 2.64E-4 1.59E.7 6.80£?7 5.966-6 2

Te-. S. S.69E.8 1. 54E-9 1.60£-B S.49£-B 7.596.?

Te- 127. 1. 77E+9 4.78E-8 4.24*-8 5.06E-9 1.44E.9 2. 116E8 Te-12? 1.21E-9 1.66E-8 Te-129m 1. 8169 5.04 E.8 5.82E-8 S. 30E. 9 2.20E69 2.806.8 Te-129 7.00£. 2 4.981.2 Te-131m 2.42E-2 2.34E63 9.82E63 2.58E.2 Te-131 Te- 132 2.09E-6 9.276-5 1,35E-6 8. 60E.6 9. 336-b 1. 12E.6 1-130 3. 39E-6 6.8SE-6 7.546-4 1.02E-5 3. 20E-6 3.53E-6 1-131 1 . 66£.7 1.67E.7 5.52E-9 2.74E.7 1.496*6 9. 49E.6 1-132 1-133 6.68£-I 8. 26E- I 1.53M-2 1.386E0 3.33E-I 3.12E-1 FERMI 2 ODCM - TRM VOLUME II 7-40 Rev. 13 1

Table 7.0-4 Raipo, Grass-Cow-Meat Pathway Dose Factors ý CHILD (CONT.)

(mrem/yr per U Ci/m 3 ) for H-3 and C-14 2

(m x mrem/yr per UCi/sec) for others Nuclide ]60Dt Liver Thyroid Kidney Lunat GI-LI 7. Body 1-134 1-135 Ca-134 9. 22E+8 1.51E.9 4.69E-8 1.68ME.,8 B. ISX6 3. 19E-6 Cs-136 .59E-7 4. 37E-7 2.33E-7 3.' 47E6 1 . 54#.6 2. 83E+7 Cs-137 1. 33E-9 1. 28E,9 1.88÷

4. 16E÷8 1 . 50E+8 7.99E*6 Cm-138 ga-139 Ba- 140 4. 39E*7 3. SEeI4 I.25£E4 2.29E+4 2.22E,? 2. 56*E6 B9-141 1

R-- 42 Ia- 140 S.41E-2 1.89E-2 5.27E.2 6.38E-3 La- 142 Ce-I41 2. 22,E4 1.I11E.4 4 .84E.3 I .38E.7 1. 64E+3 Ce-143 3. 30E-2 1. 79E+ I 7. 51E-3 2.62E.2 2. 59E-3 Ce- 144 2. 32E+6 7.26E+5 4.02E÷5 1.89E+8 1. 24E£S 4

Pr-1 3 3. 39E,4 1. 02E+.4 5. 51 E3 3. 66E-7 1. 68E#3 Pr-144 Nd-147 1. 17E÷4 9. ASE-3 5.20E+3 1. 50E7 7.34E£.2 W4-187 3. 36E-2 1.99E-2 2.79E+0 S.92E-3 Np-239 4. 20E-I 3.OZE-2 8.73E-2 2.23E÷3 2. 12E-2 FERMI 2 ODCM - TRM VOLUME II 7-41 Rev. 13 I

Table 7.0-4 Raipo, Vegetation Pathway Dose Factors - ADULT 3

imrem/yr per YLCi/m ) for H-3 and C-14 2

(m x mrem/yr per U1Ci/sec) for others Nuclide Bane Liver Thyroid. Kidney Lung GI-LLI T.Body H-3 - 2.26E-3 2.26E.3 2.26E-3 2.26E23 2.26E-3 2.26E.3 C-14 8.97E-5 1.79E*5 1.79E+5 1.79E+5 1.792*5 1.79E+5 1.79E+5 Na-24 2.76E-5 2.76E,5 2.76E25 2.76E+5 2.76E.5 2.76E+5 2.76£-S P-32 1.40E+9 8.73E*7 - - 1.58E+8 5.42E÷7 Cr-Si - - 2.79E-4' 1.03E-4 6.19E*4 1.17E-7 4.662E4 Hn-54 - 3.11E+8 9.27E-7 - 9.54E.8 5.94E-7 mn-56 - 1.61E+1 2.04E+1 - 5.13E+2 2.852,0 Fe-55 2.09£÷8 1.45E*8 8-.06E*7 8.29E+7 3.37E.?

Fe-59 1.27E28 2.992*8 - 8.35E.7 9.96E+8 1.14E+8 Co-57 - 1.17E-7 - 2.972*8 1.95E*7 Co-58 - 3.09E*7 - - 6.262*8 6.92E+7 Co-60 - 1.67E-8 - - - 3.14E-9 3.69E+8 Ni-63 1.04E.10 7.21E+8 - - - 1.50E+8 3.492.8 Ni-65 6.15E-1 7.99E*0 - - - 2.03E+2 3.652*0 CU-64 - 9.272*3 - 2.34E-4 - 7.90E+5 4.35E-3 Zn-65 3.17E*8 1.01E-9 - 6.75£*8 - 6.362*8 i.56E*8 9

Zn-6 8.75E-6 1.67E-5 - 1.09E-5 - 2.51E-6 1.16E-6 2

Br-8 3

- 1.73E+6 1.51E+6 Br-B 4 - 4.63E+0 3.21E*0 Br-8 Br-8S - -

Rb-86 2.19-8 - 4.32E-? 1.02E-8 Rb-SB --

Rb-89 ... .

8 Sr- 9 9.96E29 - 1.60E.9 2.86E-8 Sr-90 6.05E+11 - 1.75E+10 1.48E-11 Sr-91 3.202,.5 - 1.52E+6 1.29E*4 Sr-92 4.27E.2 - 8.46E+3 1.85E+1 Y-90 1.33E*4 - 1.41E+8 3.56E-2 Y-91u 5.83E-9 - 1.71E-8 -

Y-91 5.1326 -- 2.82E÷9 1.17E-5 Y-92 9.01E-1 - 1.58E÷4 2.63E-2 Y-93 1.74E+2 - 5.52E+6 4.80E+0 Zr-95 1.19E.6 3.81E+5 - 5.97E+5 - 1.21E-9 2.58E25 Zr-97 3.33E+2 6.73E*1 - 1.02E+2 - 2.082*7 3.08E41 Nb-95 1.42E.5 7.91E.4 - 7.81E.4 - 4.80E÷8 4.25E-4 Nb-97 2.90E-6 7.34E-7 - B.5627 - 2.71E-3 2.68E-7 Mo-99 - 6.25E÷6 - 1.41E.7 - 1.45E-7 1.19E-6 Tc-99m 3.06E*0 8.66£÷0 - 1.32E+2 4.242*O 5.12E*3 1.10E+2 Tc-10 -

Ru-103 4.80E-6 - - 1.83E.7 - 5.61E+8 2.07E+6 Ru-105 5.392*1 - - 6.96E*2 - 3.30E-4 2.13E*1 Ru-1O6 1.932÷8 - - 3.72E÷8 - 1.25E-10 2.44E-7 Rh-103m - -

Rh-1O6 - -

AJ-110. 1.06E-7 9.76E26 1.92E+7 3.98E+9 5.80E26 Sb-124 1.04E÷8 1.96E*6 2.52E*5 - 8.08E.7 2.95E÷9 4.11E-7 Sb-125 1.36E.8 1.52E46 1.39E,5 - 1.05E-8 1.50E+9 3.25E.7 Te-125m 9.b66-7 3.50E-7 2.90E,7 3.93E*8 - 3.862÷8 1.29E.7 Te-127m 3.49E-8 1.25E+8 8.92E÷7 1.42E,9 - 1.172*9 4.26E+7 Te-127 5.76E.3 2.07E*3 4.27E-3 2.352.4 4.54E25 1.25Z-3 Te-129& 2.55£E8 9.50E.7 8.75E+7 1.06E-9 1.282.9 4.032.7 Te-129 6.65E-4 2.50E-4 5.IOE-4 2.79E-3 5.02E-4 1.62E-4 Te-131. 9.12E-5 4.462'5 7.066>5 4.52E.6 4.43E.7 3.722*5 Te-131 - -

2 Te-13 4.29E+6 2.77E-6 3.06E+6 2.67E-7 1.31E*8 2.60E-6 1-130 3.962-5 1.172*6 9.902?7 1.82E+6 - 1.012*6 4.612'S 1-131 0.09E.7 1.162*8 3.79E,10 1.98E*8 - 3.05E+7 6.63E27 1-132 5.74E*1 1.542*2 5.38E.3 2.45E,2 - 2.89E+1 5.38E21 1-133 2.12E*6 3.69E*6 5.42E.8 b.44E26 - 3.31E*6 1.12E÷6 FERMI 2 ODCM - TRM VOLUME I! 7-42 Rev. 13

Table 7.0-4 Raipo, Vegetation Pathway Dose Factors - ADULT (CONT.)

(mrem/yr per gCilm 3 ) for H-3 and C-14 (M 2 x mrem/yr per ,UCi/sec) for others Nucl ide bone Liver Thyroid Xidney Lung CI-u-j T. body 1-134 1.06E-4 2.88E-4 5.OOE-3 4.59E-4 2. 51E-7 1. 031-4 1-135 4. OE84 1.071.5 7.04E.6 1.7 11+5 1.21 £+ 5 3. 94E.4 Cz- 134 4. 66E+9 1. 11E+10 3.59E-9 1. 19E.9 1. 94E.8 9.07E19 Cm-136 4. 20E-7 1.66E-0 9. 24E.7 I. 27E.7 1. 89t.7 1. 19E+8 Cz-137 6. 36E9 8. 70E.9 2. 951.9 9.81 L+8 1. 68E.8 5. 70E.9 Co-138 ba-139 2. 95F-2 2. 10E-5 1.96E-5 1.19E-5 5.23E-2 B. 64E-4 Ba-140 1. 29E-8 1. 62E+5 5. 49E.4 9. 25E14 2. 65E+8 8.43E.6 Ba-141 Ba- 142 La-140 1. 97t+3 9.921.2 7.281+7 2. 62E+2 La-142 1. 40E-4 6.35E-5 4.649-1 1. 5S8-5 Ce-141 1. 96E+5 1. 33E+5 6. 17E.4 5.08F+8 1. 511.4 Ce- 143 1.00E-3 7.42E.+5 3.26E.2 2.77E+7 8.21E+1 Ce-144 3. 29E£7 1. 38E.7 8. 16E16 1.1 10 1.77£E6 Pr-143 6. 34E÷4 2. 54E.4 1.47E+4 - 2.78E+8 3.14E.3 Pr-144 Nd-147 3. 34E+4 3. 86E.4 2.25E+4 - 1.85E÷8 2.31E-3 W-,187 3. 82E+4 3. 19E.4 1.05E+7 1.12E+4 Hp-239 i .42E+3 1. 40E.2 4.37E+2 2.87r.-7 7.721E-FERMI 2 ODCM - TRM VOLUME II 7-43 Rev. 13 1

Table 7.0-4 Raipo, Vegetation Pathway Dose Factors - TEENAGER (mrem/yr per uCi/m 3 ) for H-3 and C-14 2

(m x mrem/yr per /-tCi/sec) for others Nuclide Bone Liver Thyroid Kidney Lung GI-LLI T. Body 1H-3 - 2.59E£3 2.59E-3 2.59E-3 2.59E+3 2.59E+3 2.59E'3 C-14 1.45E-6 2.91E.5 2.91E-5 2.91E-5 2.91E+5 2.91E-5 2.91E+5 Na-24 2.451*5 2.45ES 2.45ES 2.5.E55 2.A5£÷5 2.45E-5 2.45E.5 P-32 1".61E+9 9.96E-? - 1.3SE*8 6.23E.7 Cr-51 - 3.4E+4 1.36E+4 8.8SE-4 1.004E+7 6.20E+4 Hn-5i - 4.52E+8 1.35£.8 - 9.27£.B 8.97E.7 Hn-S6 - 1.45E+I 1.83E.1 - 9.54E+2 2.58E.0 Fe-55 3.25E+8 2.31E.8 1.46E+8 9.98E17 5.38E+7 Fe-59 1.81E+B 4.22E+8 1.33E+8 9.98E+8 1.63E+8 Co-57 - 1.79E17 - 3.34E£8 3.OOE7 Co-SB - 4.38E.7 6.04E-8 1.01E*8 Co-60 - 2.49E-8 3.24E÷9 5.60E.8 Hi-63 1.61E+10 1.13E.9 1.81E+8 5.45E.8 Ni-65 5.73E+I 7.32E-0 3.97E+2 3.33£*O Cu-64 - g.40E63 2. 12E.4 6.51E-5 3.95E*3 Zn-65 4.24E+$ 1.47E+9 9. 411.8 6.23E+8 6.86£-8 Zn-69 8.19E-6 1.56E-5 1.02E-5 2.88E-5 1.09E-6 Br-82 - 1.33E-6 Br-83 - 3.01E*0 Br-8s, Br-85" Rb-B6 - 2.73E£b 4.05E-7 1.28E.8 Rb-88 Rb-V9 Sr-B9 1.51E+10 1.80E+9 4.33148 Sr-90 7.51E.11 2.11E+10 1.85E,11 Sr-91 2.99+5 - 1.36E+6 1.19E.4 Sr-92 3.97E+2 1.01E÷4 1.69E11 Y-90 1.24E+4 1.02E+8 3.34E+2 Y-91m 5.43E-9 2.56E-7 -

Y-91 7.87E+6 3.23E-9 2.11E+5 Y-92 2.32E*4 2.45E-2 Y-93 1.63E+2 4.98E+6 4.47E+O Zr-95 1.74E+6 5.49E÷5 8.07E+5 1.27E-9 3.78E+S Zr-97 3.09E+2 6.11E+1 9.261+1 2.81E-1 1.65E÷7 Wb-95 1.92E+5 1.06E+5 1.03E.5 - 4.551+8 5.86E+4 Xb-97 2.69E-6 6.67E-7 7.80E-7 - 1.59E-2 2.44E-7

?o-99 - 5.741*6 1.31t+7 - 1.03E+7 1.09E.6 Tc-99m 2.70E+0 7.54E10 1.12E.2 4.19E-0 4.95E+3 9.77E-1 Tc-1Ol Ru-1O3 6.a71*6 - 2.42E.7 5.74E*5

- 2.94E.6 Ru-105 5.00E-1 - 6.31£E2 - 4.04E-4 1.94E+1 Ru- 106 3.09£+8 - 5.97.-8 - 1.48E*10 3.90E-7 Rh-103.

Rh-106 AS-11O. 1.52E+7 1.44E.7 - 2.74E+7 - 4.04E+9 8.74E+6 Sb-124 1.551*8 2.85£*6 3.51£*5 - 1.35E-8 3.11E+9 6.03E.7 Sb-125 2.14E18 2.34E.6 2.04E.5 - 1.88E*8 1.66E*9 5.00E-7 Te-125m 1.481+8 5.34E,7 4.14E+7 - - 4.376E8 1.98E-7 Te-127m 5.51E+8 1.961*5 1.31.8 2.24E.9 - 1.37E+9 6.56E-7 Te-127 5.43E+3 1.92E-3 3.74E*3 2.20E+4 4.19E-5 1.17E*3 Te-129% 3.67E*5 1.36E*8 1.18E-8 1.54E.9 1.38E*9 5.81E,7 Te-129 6.22.-4 2.32E-4 4.45E-4 2.61E-3 3.40E-3 I.SIE-4 Te-131m 8.441.5 4.05E-5 6.09E+5 4.22E+6 3.25E*-; 3.38E-5 Te-131 Te-132 3.90E+6 2.47E.6 2.60£E6 2.37E+7 7;82E,7 2.32E-6 1-130 3.54E+5 1.02E+6 8.35E.7 1.58E-6 7.87Z+5 4.091+5 1-131 7.70E17 1.08E-8 3.14E.00 1.85E÷8 2.13E.7 5.79E-7 1-132 5.18E+1 1.36E#2 4.57E*3 2.14E-2 5.91.11 4.87E.1 1-133 1.97E.6 3.34E'6 4.66E.8 5.86E*6 2.531+6 1.02E.6 FERMI 2 ODCM - TRM VOLUME II 7-44 Rev. 13 1

Table 7.0-4 Raipo, Vegetation Pathway Dose Factors - TEENAGER (CONT.)

(mrem/yr per YCi/m 3 ) for H-3 and C-14 (m 2 x mrerm/yr per /UCi/sec) for others Mucl ide DOne Liver Thyroid Kidney Lunt Cl1-LUI 7. body 1-134 9. 59E-5 2. 34E-4 4. 24E-3 4.01E-4 3. 35E-6 9. 13E-5 1-135 3. 68E+4 9.4B9E4 6. 10E-6 1. 50. 5 1.05E+5 3. 52E-4 Cs-134 7.09E*9 1.67E÷10 5.30E+9 2.02E£9 2.08SE8 7. 74E+9 C.-136 4.29E-7 1. 69E.8 9. 19E.7 1 .45E+7 1.36E÷7 1. 13E÷8 Cs-137 1.01E-10 1. 35E10 4. 59E+9 1. 78E-9 1. 92E+8 4. 69E-9 Co-138 8.- 139 2. 77E-2 1. 95E-5 1.84E -5 1.34E-5 2.47E--1 8.081-4 3.-1 40 1. 3&E£8 1.69E+5 5. 75E£4 1. 14E.5 2. 13E+8 8.91E#6 Ba-141 Ba- 142 La- 140 1. 80E-3 8.84 .£÷2 5.08E£7 2. 35E*2 La-142 1. 28E-4 5.69E-5 1.73E+0 1.425-5 Ce-141 2. 82E£5 1.8S£*5 8. 86E+4 5. 38E+8 2. 16E+4 Ce-143 9.37E+2 6.82E- 5 3.06E*2 2.0SE.7 7.62Et1 Ce-144 5. 27E+7 2. 18E£7 1. 30E.7 1. 33E-10 2.83E.6 Pr-143 7. 12E.4 2. 84E+4 1. 65E.4 2. 34t£8 3. 55E+3 Pr-t44 Nd-147 3. 63E+4 3. 94EZ4 2. 32E.4 1.42E÷8 2. 36E.3 W-187 3. 55E.4 2. 90E+4 7. 84E+6 1. 02E+4 Np-239 1. 38E+3 1. 30E+2 4.09£E2 2. 10E+7 7.24E+ 1 FERMI 2 ODCM - TRM VOLUME II 7-45 Rev. 13

Table 7.0-4 Raipo, Vegetation Pathway Dose Factors - CHILD (mrem/yr per gCi/m 3 ) for H-3 and C-14 2

(m x mrem/yr per jICi/sec) for others Nucl ide Bone Liver Thyroid Kidney Lung GI-LLI T. Body N-3 4.01E-3 4.016E3 4.01E+3 4.011E3 4..01E+3 4.OIE.03 C- 14 3. 5OE-6 7.0 1E.5 7.01E-5 7.01E.5 7. 01£E.5 7.011.5 7.01E+5 Ma-24 3.83E+5 3.83E.5 3. 83£E5 3.83E£ S 3. 83£+ 5 3.83E.5 3. 83E15 P-32 3. 37£+9 1. 58£+8 9.30£E7 1. 30E.8 Cr-SI 6. 54E-4 I.79£.4 I. 19E.5 6.25£E- 1. 18-5 Mn-54 6. 61E.8 1. 85£+8 S.5SSI.. 1.76E18 mn-56 I. 90£-I 2.29£. I 2.75E+3 4. 28E.0 Fe-S 5 8. 00E-8 4.24E-8 2.40E.8 7.86£.7 1. 31E.8 Fe-59 4.01£E-8 6.49E-8 1 .88E.8 6. 76E+8 3.23E18 Co-57 2.99£E7 2.6 5.E8 6.04E+7 Co-58 6.47E£? 3. 77E-8 1. 98E+8 Co-60 3. 78E.8 2. 10£.9 I.12E.9 Ni-63 3. 95E£ 10 2. 11E+9 1.42E-8 1 . 34E.9 Ni-65 1 .05£E2 9. 89E+0 1.21E+3 5. 771.0 Cu-64 I. 11 E*4 2. 68E.4 5. 20E£ 5 6. 69E13 Zn-6.5 8. 12E+8 2. 16E-9 1. 36E-9' 3. 80£-8 1 .35E+9 Zn-69 1. 51E-5 2. 18£-5 1. 32E-5 1.38E-3 2.02£-6 Br-92 2.04+b6 Br-83 S.551.O Br-84 Br-85 Rb-86 4. 52E.8 2. 91E+7 2.78E+8 Rb-8B Rb-89 Sr-89 3. 59£E 10 1. 391÷9 1.03E-9 Sr-90 1.24E+12 1.67E+10 3. 15E1 11 Sr-91 5. 50E.5 1.21E*6 2. 081.4 Sr-92 7.28E£2 1. 38E+4 2.92÷1-Y-90 2. 30£E4 6. 56E+7 6. 17E+2 Y-91m 9. 94E-9 1. 958-5 2.49E+9 5.016+5 Y-91 1.87E7 Y-92 1. 56E+O 4.511E+4 4. 46E-2 Y-93 3.01£.2 4.48E+6 8.251+0 Zr-95 3. 90E£6 8. 58E.5 1.23E.6 B. 951.8 7.64E+5

5. 64E£2 8. 15£11 1. 17L.2 1.23£.7 4.81E.1 Zr-97

4. 10E+5 1.59£-S 1. 50E15 2. 95£.8 1. 14E-5 Nb-95 Nb-97 4. 90E-6 8.85E-7 9.82E-7 2. 73L-1 4.13E-7

)o-99 7. 83E.6 1.67E£7 6. 48E+6 1.94E+6 Tc-99% 4.65£40 9. 12E+O 1. 33E-2 4.631+0 5.19£.3 1. 51£.2 Tc- 101 Ru- 103 1. 55E£7 3. 89£.7 3. 99E+8 Ru-¶05 9. 17E- 1 8.06E-2 5. 98£'4 3.33E+ 1 Ru- 106 7. A S£8 I .01E+9 1. 16E+40 9. 30E.7 Rh- 103m Rh- 106 2.17E.7 4.05£.? 2. 58.E9 1.74E£.

AS.-110. 3.22£. 7

3. 52£L &. 57E+6 7. 74.5 1. 98E8 2. 20£-9 1.23E1B Sb-124

4. 99E88 3. 85£E6 2. 78188 1. 19E-9 I .05E18 Sb-125 Te- 125m 3. 51E+8 9. 50E-7 9.84E+? 3. 38E.8 6.67£.?

Te-127m 1. 32E÷9 3. 56E-8 3. 16E.8 3. 771.9 1.07E-9 1.57E-8 Te-127 1.00E.4 2. 70E3 6. 93E.3 2,85.E4 3.91E.5 2. 15E.3 Te-129. 8.54E.8 2. 39E-8 2. 7 5E.8 2. 511E9 1.04 E 9 1. 33E.8 Te-129 15.E£-3 3. 22£-' 8. 22E-4 3.37£-I 7. 17£-2 2. 74E-4 Te-131m 5. 33E-5 1.10E-6 5. 16E-6 2. 16E£? 5. 686-5 Tc-131 Te- 132 6.98E+6 3.09£.6 4.50E£6 2.87E,7 3.11£E0 3. 73E.,6 1-130 6.21E-5 1.26E-6 1.38E£B 1. 88.-6 5.87E.5 6. IS7E,5 1.44E÷8 4.76E.10 2. 36E.8 1.28£-7 8.18£.?

1-131 1. 6 3E8 1-132 9.20E+1 1.69E.2 7.84E£3 2. 59+.2 1.99E.2 7 .77E- 1 1-133 3. 59E.6 4.6414E 8.25E-8 7. 40E.6 1. 79E£6 1. 68E-6 FERMI 2 ODCM - TRM VOLUME II 7-46 Rev. 13

Table 7.0-4 Raipo, Vegetation Pathway Dose Factors - CHILD (CONT.)

3 (mrem/yr per uCi/m ) for H-3 and C-14 2

(m x rnrem/yr per gCi/sec) for others Nuclide gone Liver Thyroid KIdney Luns GI-LLI T.ISody 1-134 1.70E-4 3, 16E-4 7.28E-3 4. 841-4 2. 10-4 1.461-4 1-135 6. 54E-4 1. 18E.5 1.04E+7 1.81 1.5 8.98E+4 5.57E+4 Cs-134 1. 60E. 10 2. 63E-10 8. 141.9 2.92E+9 1.42E+8 5. 541.9 C6-136 8.06E+7 2. 221.8 1. 18E+8 1.76E17 7. 79E+6 1.43E+8 Cs-137 2. 39E. 10 2.29E+10 7. 46E.9 2. 68E.9 1. 43E.8 3.38E+9 CS-138 8a-139 5. 11E-2 2.73E-5 2.38£-S 1.6 1-5 2. 951.O 1.48E-3

2. 43E+5 1,.45E-5 sa-140 2.77E+8 7 . 90E+4 1.40E.3 1.62E.7 Ba- 141 Ia-142 La- 140 3.23£*3 1.13E+3 3.15E.7 3. 811+2 LA- 142 2. 32E-4 7.40E-5 1.47E-1 2.32E-5 Cc-141 1. 231.5 6. 14E.4 2. 691-4 7.66E.7 9.12E+3 Ce-143 1. 73E+3 9. 36E.5 3.93E.2 I. 37E.7 1. 36E.2 Ce-144 1.271*8 3.98E0) 2.21E+ 1.04E+10 6. 7 8E+6 Pr-143 1. 48E. 5 4.46E.4 1.601+8 7. 3 7E+3 Pr-144 Hd-147 7. 16E+4 5.80r+4 3. 18E14 9.18E+7 4. 49E+3 W-187 6. 471.4 3.83E+4 5. 38E.6 1.72E+4 Np-239 2. 55E-3 1.983E2 5. 30E-2 1 . 36E+7 1.29E.2 FERMI 2 ODCM - TRM VOLUME II 7-47 Rev. 13 1

Table 7.0-4 Raipo, Ground Plane Pathway Dose Factors (mn2 x mrem/yr per /LCi/sec)

Nuclide Any Orsan H-3 C-14 Na-24 1.21E*7 P-32 -

Cr-51 4.68E*6 Hn-54 1.34E-9 Nn-56 9.05E+5 Ee-55 Fe-59 2.75E+8 Co-58 3.82E+8 Co-60 2.16E-10 Ni-63 Ni-65 2.97E-5 Cu-64 6.09E-5 Zn-65 7.45E*8 Zn-69 Or-83 4.89E-3 Br-84 2.03£*5 Br-S5 Rb-86 8.98E-6 Rb-88 3.29E*4 Rb-89 1.21E*5 Sr-89 2.16E-4 Sr-90 Sr-91 2.19E-6 Sr-92 7.77E*5 Y-90 4.48E-3 Y-91M 1.01E-5 Y-91 1.08E+6 Y-92 1.80E+5 Y-93 1.856-5 Zr-95 2.48E+8 Zr-97 2.94E+6 Nb-95 1.366+8 Mo-99 4.05E+6 Tc-99= 1.836+5 Tc-t01 2.04E+4 Ru-103 1.09£+8 Ru-IOS 6.36E*5 Ru-106 4.21E+8 Kh- 103m-Rh-106 Ag-110. 3.47E+9 Te-125m 1,55E-6 Te-127m 9,176-4 Te-127 3.OOE+3 Te-129m 2.006*7 9

Te-12 2.60E-4 7e-13l= 8.03E-6 Te-131 2.93E-4 Te-132 4.22E-6 1-130 5.53E+6 1-131 1.72E67 1-132 1.24E+6 1-133 2.47E+6 1-134 4.49E-5 1-135 2.56E-6 Cs-134 6.75E+9 Co-136 1.49E-8 Cs-137 1.04E+10 FERMI 2 ODCM - TRM VOLUME II 7-48 Rev. 13

Table 7.0-4 Raipo, Ground Plane Pathway Dose Fadtors (CONT.)

( (m 2 x mrem/yr per UCi/sec) suclide Any Organ Cs-138 3. 59E+5 Ba-139 1 .06E+5 Ra-i 40 2.05E+7 Ba-ld.

4. ISE...d Ba- 142 4.4 9E+4 La-i140 1. 91E..7 La-142 7. 16E- 5 Ce-141 1. 36E-7 Ce- 14 3 2. 32E+6 Ce- 144 6. 95E.7 Pr-143 Pr-144 I .83E- 3 Nd-147 8.40E-6 W-187 2. 36E#6 Np-239 1 .71E+6 FERMI 2 ODCM - TRM VOLUME II 7-49 Rev., 13 1

FIGURE 7.0-1 GASEOUS RADIOACTIVE EFFLUENT MONITORING AND VENTILATION SYSTEMS DIAGRAM Key HEPA Flte charcool TKu.r Reactor o duLndg aFf G05 HIEC VACUUH Rx Mdg Exh Plenum NOTE: The HEPA and charcoal filters identified on the Standby Gas Treatment System (SGTS) are engineered safety features and are not considered Ventilation Exhaust Treatment Systems (VETS). No effluent reduction was credited in the UFSAR 10CFR50 Appendix I evaluation for filters installed in plant ventilation systems. Fermi 2 conforms to 10CFR50 Appendix I without filtration installed.

FERMI 2 00CM - TRM VOLUME II 7"-50 .END OF SECTION 7.0 Rev. 13 I

SECTION 8.0 SPECIAL DOSE ANALYSIS FERMI 2 ODCM - TRM VOLUME II 8-1 Rev. `13

8.0 SPECIAL DOSE ANALYSES

( 8.1 Doses Due to Activities inside the SITE BOUNDARY In accordance with ODOM 5.9.1.8, the Annual Radioactive Effluent Release Report submitted prior to May 1 of each year shall include an assessment of radiation doses from radioactive liquid and gaseous effluents to MEMBERS OF THE PUBLIC due to their activities inside the SITE BOUNDARY.

Two locations within the Fermi 2 SITE BOUNDARY are accessible to MEMBERS OF THE PUBLIC for activities unrelated to Detroit Edison operational and support activities. One is the over-water portion of the SITE BOUNDARY due east of the plant. Ice fishermen sometimes fish here during the winter. The other isthe Fermi 2 Visitor's Center, outside the protected area (but inside the Owner Controlled Area), approximately 470 meters SSW of the Reactor Building. The Visitor's Center is open to the public and is routinely visited by MEMBERS OF THE PUBLIC, including school tour groups on a frequency of once per year.

Conservative assumptions of locations, exposure times, and exposure pathways for assessing doses from gaseous and liquid effluents due to activities inside the SITE BOUNDARY are presented in Table 8.0-1. The calculational methods presented in 00CM Sections 7.6 and 7.7 may be used for determining the maximum potential dose to a MEMBER OF THE PUBLIC based on the above assumptions. Alternatively, the effluent concentration values of Appendix B, Table 2, of the revised 10 CFR Part 20 may be used to assess dose since these concentrations, if continuously inhaled or ingested, produce a total effective dose equivalent of 50 mrem per year.

The potential dose from the fish pathway to a MEMBER OF THE PUBLIC engaged in ice fishing within the SITE BOUNDARY is accounted for by the modeling presented in ODOM Section 6.5. Therefore, no additional special dose analyses are required for this exposure pathway for reporting in the Annual Radioactive Effluent Release Report.

8.2 Doses to MEMBERS OF THE PUBLIC -40 CFR 190 The Annual Radioactive Effluent Release Report shall also include an assessment of the radiation dose to. the likely most exposed MEMBER OF THE PUBLIC for reactor releases and other nearby uranium fuel cycle sources (including dose contributions from effluents and direct radiation from onsite sources). For the likely most exposed MEMBER OF THE PUBLIC in the vicinity of the Fermi 2 site, the sources of exposure need consider only the radioactive effluents and direct exposure contribution from Fermi 2.

No other fuel cycle facilities contribute significantly to the cumulative dose to a MEMBER OF THE PUBLIC in the immediate vicinity of the site. Davis-Besse is the closest fuel cycle facility located about 20 miles to-the SSE. Due to environmental dispersion, any routine releases from Davis-Besse would contribute insignificantly to the potential doses in the vicinity of Fermi 2.

As appropriate for demonstrating/evaluating compliance with the limits of 00CM 3.11.4 (40 CFR 190), the results of the environmental monitoring program may be used to provide data on actual measured levels of radioactive material in the actual pathways of exposure.

FERMI 2 ODCM - TRM VOLUME 1182Re.1 8-2 Rev. 13

8.2.1 Effluent Dose Calculations For purposes of implementing the surveillance requirements of ODCM 3.11.4 and the reporting requirements of ODCM 5.9.1.8, dose calculations for Fermi 2 may be performed using the calculational methods contained within this ODCM and the conservative controlling pathways and locations of Table 7.0-3. Liquid pathway doses may be calculated using Equation (6-10). Doses due to releases of radioiodines, tritium and particulates may be calculated based on Equation (7-14).

The following equations may be used for calculating the doses to MEMBERS OF THE PUBLIC from releases of noble gases. Equation (8-2) is not used for evaluating compliance with 40 CFR Part 190, since this regulation does not address skin dose. If noble gases are being released from more than one point, these equations must be used to evaluate each release point separately, and then the doses must be added to obtain the total noble gas dose.

D tb : 3.17 E-08* X/Q *-(Ki

Qi)

(8-1) and Ds= 3.17E-08* X/Q,*(Li +.1M.)

Qi]

(8-2) where:

Dtb total body dose due to gamma emissions for noble gas radionuclides (mrem)

Ds skin dose due to gamma and beta emissions for noble gas radionuclides (mrad)

X/Q atmospheric dispersion to the offsite location (sec/m3 )

Qi cumulative release of noble gas radionuclide i over the period of interest (pCi)--may be determined according to Equation (7-8) 1.67E + 01 = (1 E + 03 ml/liter) * (1 min/60 sec)

FERMI 2 ODCM - TRM VOLUME Ie 8-3 Rev. 13

Ki total body dose factor due to gamma emissions from noble 3

gas radionuclide i (mrem/yr per pCi/m )

(from Table 7.0-2)

Li skin dose factor due to beta emissions from noble gas radionuclide i (mrem/yr per pCi/m 3 ) (from Table 7.0-2)

Mi gamma air dose factor for noble gas radionuclide i (mrad/yr per pCi/m 3 ) (from Table 7.0-2) 1.1 mrem skin dose per mrad gamma air dose (mrem/mrad) 3.17 E - 08 1/3.15 E + 07 yr/sec Average annual meterological dispersion parameters or meterological conditions concurrent with the release period under evaluation may be used (e.g., quarterly averages or year-specific annual averages).

8.2.2 Direct Exposure Dose Determination From evaluations performed in the Fermi 2 Environmental Report, Section 5.3.4, the direct exposure to the highest offsite location from the Turbine Building N-16 skyshine dose has been calculated to be approximately 3 mrem/year. The introduction of hydrogen injection at Fermi 2 in 1997 (hydrogen water chemistry) tends to increase direct exposure. Direct exposure to offsite or onsite individuals may be evaluated based on the results of environmental measurements (e.g.

area TLD and survey meter data) or by the use of a radiation transport and shielding calculational method. Only during atypical conditions will there exist any potential for significant onsite sources at Fermi 2 that would yield potentially significant offsite doses to a MEMBER OF THE PUBLIC. However, should a situation exist whereby the direct exposure contribution is potentially significant, onsite measurements, offsite measurements and calculational techniques will be used for determination of dose for assessing 40 CFR 190 compliance. The calculational techniques will be identified, reviewed, and approved at that time, and will be included in any report on doses due to such atypical conditions.

8.2.3 Dose Assessment Based on Radiological Environmental Monitoring Data Normally, the assessment of potential doses to MEMBERS OF THE PUBLIC must be calculated based on the measured radioactive effluents at the plant.

The resultant levels of radioactive material in the offsite environment are usually so minute as to be undetectable. The calculational methods presented in this.

ODCM are used for modeling the transport in the environment and the resultant exposure to offsite individuals.

FERMI 2 ODCM - TRM VOLUME II 8-4 Rev. 13

The results of the radiological environmental monitoring program can provide input into the overall assessment of impact of plant operations and radioactive effluents. With measured levels of plant related radioactive material in principal pathways of exposure, a quantitative assessment of potential exposures can be performed. With the monitoring program not identifying any measurable levels, the data provides a qualitative assessment - a confirmatory demonstration of the negligible impact.

Dose modeling can be simplified into three basic parameters that can be applied in using environmental monitoring data for dose assessment:

D = C*U*DF (8-3) where:

D = dose or dose commitment C = concentration in the exposure media, such as air concentration for the inhalation pathway, or fish, vegetation or milk concentration for the ingestion pathway U = individual exposure to the pathway, such as hr/yr for direct exposure, kg/yr for ingestion pathway DF = dose conversion factor to convert from an exposure or uptake to an individual dose or dose commitment The applicability of each of these basic modeling parameters to the use of environmental monitoring data for dose assessment is addressed below:

Concentration - C The main value of using environmental sampling data to assess potential doses to individuals is that the data represents actual measured levels of radioactive material in the exposure pathways. This eliminates one main uncertainty and the modeling has been removed - the release from the plant and the transport to the environmental exposure medium.

Environmental samples are collected on a routine frequency per the ODOM. To determine the annual average concentration in the environmental medium for use in assessing cumulative dose for the year, an average concentration should be determined based on the sampling frequency and measured levels:

c.= (C.

t) / 365 (8-4)

FERMI 2 ODCM - TRM VOLUME 1185Re.1 8-5 Rev. 13

where:

= average concentration in the sampling medium for the year Ci concentration of each radionuclide i measured in the individual sampling medium t = period of time that the measured concentration is considered representative of the sampling medium (typically equal to the sampling frequency; e.g., 7 days for weekly samples, 30 days for monthly samples).

If the concentration in the sampling medium is below the detection capabilities 0.(.e., less than Lower Limits of Detection (LLD), a value of zero should be used for Ci (Ci = 0).

Exposure - U Default Exposure Values (U)as recommended in Regulatory Guide 1.109 are presented in Table 8.0-2. These values should be used only when specific data applicable to the environmental pathway being evaluated is unavailable.

Also, the routine radiological environmental monitoring program is designed to sample/monitor the environmental media that would provide early indications of any measurable levels in the environment but not necessarily levels to which any individual is exposed. For example, sediment samples are collected in the area of the liquid discharge: typically, no individuals are directly exposed. To apply the measured levels of radioactivity in samples that are not directly applicable to exposure to real individuals, the approach recommended is to correlate the location and measured levels to actual locations of exposure.

Hydrological or atmospheric dilution factors can be used to provide reasonable correlations of concentrations (and doses) at other locations. The other alternative isto conservatively assume a hypothetical individual at the sampling location. Doses that are calculated in this manner should be presented as hypothetical and very conservatively determined - actual exposure would be much less. Samples collected from the Monroe water supply intake should be used for estimating the potential drinking water doses. Other water samples collected, such as near field dilution area, are not applicable to this pathway.

Dose Factors - DF The dose factors are used to convert the intake of the radioactive material to an individual dose commitment. Values of the dose factors are presented in NRC Regulatory Guide 1.109. The use of the RG 1.109 values applicable to the exposure pathway and maximum exposed individual is referenced in Table 8.0-2.

FERMI 2 ODCM - TRM VOLUME 1I86Re.1 8-6 Rev. 13

Assessment of Direct Exposurer Doses from Noble Gases Thermoluminescent Dosimeters (TLD) are routinely used to assess the direct exposure component of radiation doses in the environment. However, because routine releases of radioactive material (noble gases) are so low, the resultant direct exposure doses are also very low. A study* performed for the NRC concluded that it was generally impractical to distinguish any plant contribution to the natural background radiation levels (direct exposure) below around 10 mrem per year. Therefore, for routine releases from nuclear power plants the use of TLD is mainly confirmatory - ensuring actual exposures are within the expected natural background variation.

For releases of noble gases, environmental modeling using plant measured releases and atmospheric transport models as presented in ODCM Sections 7.6

.and 8.2.1 represents the best method of assessing potential environmental doses. However, under unusual conditions, direct radiation from noble gas concentrations could be sufficient to cause significant increases in TLD readings; any observed variations in TLD measurements outside the norm should be evaluated.

NUREG/CR-071 1, Evaluation of Methods for the Determination of X- and Gamma-Ray Exposure Attributable to a Nuclear Facility Using Environmental TLD Measurements, Gail dePlanque, June 1979, USNRC.

FERMI 2 ODCM - TRM VOLUME II 8-7 Rev. 13

TABLE 8-1 Assumptions for Assessing Doses Due to Activities inside SITE BOUNDARY Ice Fishing Visitor's Center Distance/ 470 meters / E 470 meters / SSW Direction:

Estimated 240 hr/yr 4 hr/yr Exposure (20 hr/week over (4 hr/visit, 1 visit Time: 3 month period) per year)

Exposure direct exposure direct exposure Pathways: from noble gases from noble gases inhalation of inhalation of tritium, iodines, tritium, iodines particulates particulates Meteorological annual average annual average Dispersion: (as determined (as determined for year being for year being evaluated) evaluated) 3 6.48E-6 sec/m

2.54E-6 sec/m 3*

Annual average X/Q values for 1991. These values are shown as examples of the range of values to be expected.

FERMI 2 ODCM - TRM VOLUME II 8-8 Rev. 13

TABLE 8-2 Recommended Exposure Rates in Lieu of Site Specific Data*

Table Reference Exposure Pathway Maximum Exposed Exposure Rates for Dose Factor Age Group from RG 1.109 Liquid Releases Fish Adult 21 kg/y E-11 Drinking Water Adult 730 I/y E-11 Bottom Sediment Teen 67 h/y E-6 Atmospheric Releases Inhalation Teen 8,000 m3 /y E-8 Direct Exposure All 6,100 h/y** N/A Leafy Vegetables Child 26 kg/y E-13 Fruits, Vegetables Teen 630 kg/y E-12 and Grain Milk Infant 330 I/y E-14 Adapted from Regulatory Guide 1.109, Table E-5. This table is not a complete list of exposure rates; other applicable values may be found in Regulatory Guide 1.109.

Net exposure of 6,100 h/y is based on the total 8760 hours0.101 days 2.433 hours 0.0145 weeks 0.00333 months per year adjusted by a 0.7 shielding factor as recommended in Regulatory Guide 1.109.

END OF SECTION 8.0 FERMI 2 ODCM - TRM VOLUME II 8-9 Rev. 13

[.

SECTION 9.0 ASSESSMENT OF LAND USE CENSUS FERMI 2 0DCM - TRM VOLUME II 9-1 Rev. 13

9.0 ASSESSMENT OF LAND USE CENSUS DATA A Land Use Census (LUC) is conducted annually in the vicinity of the Fermi 2 site. This census fulfills two main purposes: 1) Meet requirements of ODCM 3.12.2 for identifying controlling location/pathway for dose assessment of ODCM 3.11.2.3; and 2) provide data on actual exposure pathways for assessing realistic doses to MEMBERS OF THE PUBLIC.

9.1 Land Use Census as Required by ODCM 3.12.2 As required by ODCM 3.12.2, a land use census shall be conducted during the growing season at least once per twelve months. The purpose of the census is to identify within a 5 mile distance the location in each of the 16 meterological sectors of all milk producing animals, all meat producing animals, all gardens larger than 500 ft2 producing broadleaf vegetation, and the closest residence to the plant. The data from the LUC is used for updating the location/pathway for dose assessment and for updating the Radiological Environmental Monitoring Program.

If the census identifies a location/pathway(s) yielding a higher potential dose to a MEMBER OF THE PUBLIC than currently being assessed as required by ODCM 3.11.2.3 (and ODCM Section 7.7 and Table 7.0-3), this new location pathway(s) shall be used for dose assessment. Table 7.0-3 shall be updated to include the currently identified controlling location/pathway(s). Also, ifthe census identifies a location(s) that yields a calculated potential dose (via the same exposure pathway) 20% greater than a location currently included in the Radiological Environmental Monitoring Program, the new location(s) shall be added to the program within 30 days, unless permission to take samples cannot be obtained from the affected landowner. The sampling location(s),

excluding control locations, having the lowest calculated dose may be deleted from the program after October 31 following the current census. As required by ODCM 3.12.2 and 5.9.1.8, the new location/pathway(s) shall be identified in the next Annual Radioactive Effluent Release Report. The following guideline shall be used for assessing the results from the land use census to ensure compliance with ODCM 3.12.2.

9.1.1 Data Compilation

1. Compile all locations and pathways of exposure as identified by the land use census.

2. From this compiled data, identify any changes from the previous year's census. Identify the current controlling location/pathway (critical receptor) used in ODCM Table 7.0-3. Also, identify any location currently included in the REMP (Table 10-1).

FERMI 2 ODCM - TRM VOLUME II 9-2 Rev. 13

3. Perform relative dose calculations based on actual Fermi 2 gaseous I:

effluent releases for a recent period of reactor operation; using the pathway dose equations of the ODCM. In identifying the critical receptor for Table 7.0-3, all age groups and all pathways relevant to ODCM 3.11.2.3 that may be present at each evaluated location are considered. The critical receptor is assumed to be a member of the age group with the highest calculated dose to the maximally exposed organ due to 1-131, 1-133, tritium, and particulates with half lives greater than 8 days. Other receptors may have higher doses to other organs than the critical receptor has to those organs.

4. Formulate a listing of locations of high dose significance in descending order of relative dose significance. Include the relative dose significance in the listing.

9.1.3 Program Updates

1. If any receptor is identified with a higher relative dose than the current critical receptor in ODCM Table 7.0-3, this receptor and its associated location and pathways should replace the previously identified critical receptor information in Table 7.0-3.

2. The Land Use Census data should be used to revise the REMP and Section 10.0 of the ODCM in accordance with ODCM 3.12.2, Action Item b.

3. Any changes in either the controlling location/pathway(s) (critical receptor) for the ODCM dose calculations (Section 7.7 and Table 7.0-3) or the REMP (ODCM Section 10.0 and Table 10-1) shall be reported to NRC in accordance with ODCM 3.12.2, Action Items a. and b. and ODCM 5.9.1.8.

NOTE: As permitted by footnote to ODCM 3.12.2, broadleaf vegetation sampling may be performed at the SITE BOUNDARY in two locations, in different sectors with highest predicted D/Qs, in lieu of the garden census.

Also, for conservatism in dose assessment for compliance with ODCM 3.11.2.3 (see also QDCM Section 7.7 and Table 7.0-3), hypothetical exposure location/pathway(s) and conservative dispersion factors may be assumed (e.g., milk cow at 5 mile location or garden at SITE BOUNDARY in highest D/Q sector). By this approach, the ODCM is not subject to frequent revision as pathways and locations change from year to year. A verification that the hypothetical pathway remains conservative and valid is still required. Also, for NRC reporting, the actual pathways and doses should be reported along with the hypothetical. The reporting of the actual pathway and doses provides a formal documentation of the more realistic dose impact.

Note: Page content was last changed with ODCM Revision 16.

FERMI 2 ODCM- TRM VOLUME 11 9-3 Rev. 18 VI"

9.2 Land Use Census to Support Realistic Dose Assessment The LUC provides data needed to support the special dose analyses of the ODCM Section 8.0. Activities inside the SITE BOUNDARY should be periodically reviewed for dose assessment as required by ODCM 5.9.1.8 (see also ODCM Section 8.1).

Assessment of realistic doses to MEMBERS OF THE PUBLIC is required by ODCM 3.11.4 for demonstrating compliance with the EPA Environmental Dose Standard, 40 CFR 190 (ODCM Section 8.2).

To support these dose assessments, the LUC shall include use of Lake Erie water on and near the site. The LUC shall include data on Lake Erie use obtained from local and state officials. Reasonable efforts shall be made to identify individual irrigation and potable water users, and industrial and commercial water users whose source is Lake Erie. This data is used to verify the pathways of exposure used in ODCM Section 6.5.

END OF SECTION 9.0 FERMI 2 ODCM - TRM VOLUME 11 9-4 Rev. 13

SECTION 10.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM FERMI 2 0DCM - TRM VOLUME i3 10-1 Rev. 13

1-0.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

( The Radiological Environmental Monitoring Program (REMP) is conducted in accordance with the requirements of ODCM 3.12.1. The sampling and analysis program described herein was developed to provide representative measurements of radiation and radioactive materials resulting from station operation in the principal pathways of exposure of MEMBERS OF THE PUBLIC. This monitoring program implementsSection IV.B.2 of Appendix I to 10 CFR Part 50 and thereby supplements the radiological effluent control program by verifying that the measurable concentrations of radioactive materials and levels of radiation are not higher than expected on the basis of the effluent measurements and the modeling of the environmental exposure pathways. Guidance for the development of this monitoring program is provided by the NRC Radiological Assessment Branch Technical Position on Environmental Monitoring, Revision 1, November 1979.

10.1 Sampling Locations Sampling locations as required by ODCM 3.12.1 are described in Table 10.0-1.

,NOTE: For purposes of implementing ODCM 3.12.2, sampling locations will be modified as required to reflect the findings of the annual land use census as described in ODCM Section 9.1 and as required by other contingencies (e.g. unavailability of milk from a listed location). Such changes will be documented in plant records and reflected in the next ODCM revision, the next Annual Effluent Release Report, and the next Annual Radiological Environmental Operating Report. Also, if the circumstances of such changes involve a possible change in the maximally exposed individual evaluated for ODCM Control 3.11.2.3, the identity of this K individual will be reevaluated.

10.2 Reporting Levels ODCM 3.12.1, Action b, describes criteria for a Special Report to the NRC if levels of plant-related radioactive material, when averaged over a calendar quarter, exceed the prescribed levels of ODCM Table 3.12.1-2. The reporting levels are based on the design objective doses of 10 CFR 50, Appendix I (i.e., the annual limits of ODCM 3.11.1.2, 3.11.2.2 and 3.11.2.3), In other words, levels of radioactive material in the respective sampling medium equal to the prescribed reporting levels are representative of potential annual doses of 3 mrem, total body or 10 mrem, maximum organ from liquid pathways; or 5 mrem, total body, or 15 mrem, maximum organ for the gaseous effluent pathway. These potential doses are modeled on the maximum individual exposure or consumption rates of NRC Regulatory Guide 1.109.

The evaluation of potential doses should be based solely on radioactive material resulting from plant operation. As stated in ODCM 3.12.1, Action b, the report shall also be submitted if radionuclides other than those in ODCM Table 3.12.1-2 are detected (and are a result of plant effluents) and the potential dose exceeds the above annual design objectives. The method described in ODCM Section 8.2.3 may be used for assessing the potential dose and required reporting for radionuclides other than those in ODCM Table 3.12.1-2.

FERMI 2 ODCM - TRM VOLUME Ii 10-2 Rev. 13

10.3 Interlaboratory Comparison Program A major objective of this program is to assist laboratories involved in environmental radiation measurements to develop and maintain both an intralaboratory and an interlaboratory quality control program. This is accomplished through a laboratory intercomparison study ("cross-check") program involving environmental media and a variety of radionuclides with activities at or near environmental levels.

Simulated environmental samples, containing known amounts of one or more radionuclides, are prepared and routinely distributed to Detroit Edison's contract environmental laboratory, which performs the required analyses. The analysis results are then compared to the known concentrations in the samples. The program thus enables the laboratory to document the precision and accuracy of its radiation data, and identify instrument and procedural problems.

The environmental laboratory is required to participate in an Interlaboratory Comparison Program and to submit QA Program Progress Summary Reports to Detroit Edison on an annual basis. These reports contain performance data summaries on blind spiked analyses, and explanations of deviations from expected results. A summary of the Interlaboratory Comparison Program results obtained is required to be included in the Annual-Radiological Environmental Operating Report pursuant to ODCM 5.9.1.7.

Participation in an Interlaboratory Comparison Program ensures that an independent check on the precision and accuracy of the measurements of radioactive material in environmental sample matrices is performed as part of the QA Program for environmental monitoring in order to demonstrate that the results are valid for the purpose of Section IV.B.2 of Appendix I to 10 CFR Part 50.

FERMI 2 ODCM - TRM VOLUME II 10-3 Rev. 13

TABLE 10.0-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM FERMI 2 SAMPLE LOCATIONS AND ASSOCIATED MEDIA KEY 1- T TLD Locations (Pg. 10-5 through 10-9) 2- S Sediments Locations (Pg. 10-10) 3- F Fish Locations (Pg. 10-10) 4- M Milk Locations (Pg. 10-11) 5- DW Drinking Water Locations (Pg. 10-12) 6- SW Surface Water Locations (Pg. 10-12) 7- GW Ground Water Locations (Pg. 10-12) 8- API Air Particulate/Iodine Locations (Pg. 10-13) 9- FP Food Products Locations (Pg. 10-14)

FERMI 2 ODCM - TRM VOLUME II 104 Rev. 13

TABLE 10.0-1 Radiological Environmental Monitoring Program, Fermi 2 Sample Locations and Associated Media Direct Radiation T1 NE/38° 1 3 mi Estral Beach Pole on Lakeshore, 23 Poles S of Lakeview Direct Radiation (Special Area)

T2 NNE/220 1.2 mi East of termination of Brancheau St. on post Direct Radiation Q (Special Area)

T3 N190 1.1 mi Pole, NW Corner of Swan Boat Club Fence Direct Radiation Q

i (Special Area)

T4 NNW/337 0 0.6 mi Site Boundary and Toll Rd, on Site Fence-by API #2 Direct Radiation Q T5 NW/3M37 0.6 mi Site Boundary and Toll Rd, on Site Fence by API #3 Direct Radiation Q 0

T6, WNW/294 0.6 mi Site boundary fence at south end of N. Bullit Rd. Direct Radiation Q 0

T7 W/270 14.0 mi Pole, at Michigan Gas substation on N. Custer Rdl, 0.66 miles W of Direct Radiation Q

_ _ Doty Rd. (Control)

T8 NW/305 0 1.9 mi Pole on Post Rd. near NE Corner of Dixie Hwy. and Post Rd. Direct Radiation Q T9 NNW/334 0 1.5 mi Pole, NW Corner of Trombley and SwanView Road Direct Radiation Q T1o N/6" 2.1 mi Pole, S Side of Masserant - 2 Poles W of Chinavare Direct Radiation Q T 1 NNE/23 0 6.2 ml Pole, NE Corner of Milliman and Jefferson Direct Radiation Q T12: NNE/29 0 6.3 ml Pointe Mouillee Game Area - Field Office, Pole near Tree, N Area of Direct Radiation Q

-,. *"Parking Lot T13 L N/356 0 4.1 mi Labo and Dixie Hwy - Pole on SW Corner with Light Direct Radiation Q 0

114 NNW/337 4.4 mi Labo and Brandon - Pole on SE Corner near RR Direct Radiation Q Note: Itage content was last changed with ODCM Revision 16.

FERMI 2 ODCM - TRM VOLUME II 10-5 Rev. 18

TABLE 10.0-1 Radiological Environmental Monitoring Program, Fermi 2 Sample Locations and Ass6ciated Media Direct Radiation T15 NW/315 0 3.9 mi Pole, behind building at the corner of Swan Creek; and Mill St. Direct Radiation Q T16 WNW/2830 4.9 ml Pole, SE corner of War and Post Rds. Direct Radiation Q T17 0 W/271 4.9 mi Pole, NE Corner of Nadeau and LaPrad near Mobile Home Park Direct Radiation Q T18i 0 WSW/247 4.8 mi Pole, NE Corner of Mentel and Hurd Direct Radiation Q T19 0 SW/236 5.2 mi 1st Pole N of State Park Rd on E side of-Waterworks Rd Direct Radiation Q T20 \AISW/257 0 2.7 mi Pole, S Side of Williams Rd. - 8 Poles W of Dixie Hwy. (Special Area) Direct Radiation Q T21 V'WSW/239 0 2.7 mi Pole, N Side of Pearl at Parkview - Woodland Beach (Special Area) Direct Radiation Q T22 i S/172 0 1.2 mi Pole, N Side of Pointe Aux Peaux 2 Poles W of Long - Site Boundary Direct Radiation Q T23 0 SSW/195 1.1 mi Pole, S Side of Pointe Aux Peaux - 1 Pole W of Huron next to Vent. Direct Radiation Q Pipe - Site Boundary T24 i SW/225 0 1.2 mi Fermi Gate along Pointe Aux Peaux Rd.- on fence wire W of Gate -

.. _____Site Direct Radiation Q Boundary T25 I WSW/252 0 1.5 mi Pole, Toll Rd. -12 Poles S of Fermi Dr. Direct Radiation Q T26 0 WSW/259 1.1 mi Pole, Toll Rd. - 6 Poles S of Fermi Dr. Direct Radiation Q T27 SW/225 0 6.8 mi Pole, NE Corner of McMillan and East Front St. (Special Area) Direct Radiation Q T28 i SW/229° 10.7 mi Pole, SE Corner of Mortar Creek and LaPlaisance (Control) Direct Radiation Q T291 0 VVSW/237 10.3 mi Pole, E Side of S Dixie, 1 Pole S of Albain (Control) Direct Radiation Q Note: ýage content was last changed with ODCM Revision 16.

7 FERMjI 2 ODCM - TRM VOLUME il 10-6 Rev. 18

TABLE 10.0-1 Radiological Environmental Monitoring Program, Fermi 2 Sample Locations and Associated Media Direct Radiation Station Meteorological Distance from Number Sector/Azimuth Reactor (Approx.) Description Media Frequency Direction T30 WSW12470 7.8 mi Pole, St. Mary's Park near foot bridge (park is near corner of Elm and Direct Radiation Q Monroe streets)

T31 WSW/2550 9.6 mi 1st Pole W of Entrance Drive Milton "Pat" Munson Recreational Direct Radiation Q Reserve - N. Custer Rd. (Control)

T32 WNW/2950 10.3 mi Pole, Corner of Stony Creek and Finzel Rds. Direct Radiation Q T33 NW/3170 9.2 mi Pole, W Side of Grafton Rd. 1 Pole N of Ash/Grafton Intersection Direct Radiation Q T34 NNW/338 0 9.7 mi Pole, W Side of Port Creek, 1 pole S of Will Carleton Rd. Direct Radiation Q T35 N/359 0 6.9 mi Pole, S Side of S. Huron River Dr. across from Race St. (Special Direct Radiation Q

____________________Area) ___ __

T36 N1358 0 9.1 mi Pole, NE Corner of Gibraltar and Cahill Rds. Direct Radiation Q T37 NNE/210 9.8 mi Pole, S Corner of Adams and Gibraltar (across from Humbug Marina) Direct Radiation Q T38 WNW/2940 1.7 mi Residence - 6594 N. Dixie Hwy. Direct Radiation Q T39 S/1760 0.3 mi SE Corner of Protected Area Fence (PAF) Direct Radiation Q T40 S/1700 0.3 mi Midway along OBA - PAF Direct Radiation Q T41 SSEI161o 0.2 mi Midway between OBA and Shield Wall- PAF Direct Radiation Q T42 SSEJ1490 0.2 mi Midway along Shield Wall - PAF Direct Radiation Q T43 SE/1310 0.1 mi Midway between Shield Wall and Aux Boilers - PAF Direct Radiation Q T44 ESE/1090 0.1 mi Opposite OSSF Door - PAF Direct Radiation Q FERMI 2 ODCM - TRM VOLUME II 10-7 Rev. 13 1

TABLE 10.0-1 Radiological Environmental Monitoring Program, Fermi 2 Sample Locations and Associated Media Direct Radiation Station Meteorological Distance from Number Sector/Azimuth Reactor(Approx.) Description Media Frequency Direction T45 E/86 0 0.1 mi NE Corner- PAF T46 ENE/67 0 0,2 ml NE Side Barge Slip - on Fence Direct Radiation Q T47 S/1850 0.1 ml South of Turbine Bldg. rollup door on PAF Direct Radiation Q T48 SW/235o 0.2 mi 30 ft. from corner of AAP on PAF T49 WSW/2510 1.1 m. Corner of site boundary fence north of NOC along Critical Path Rd. Direct Radiation Q T50 W12700 0.9 mi Site boundary fence near main gate by the south Bultit St. sign Direct Radiation Q T51 N/3 0 0.4 ml Site boundary fence north of North Cooling Tower Direct Radiation Q T52 NNE/20 0 0.4 mi Site boundary fence at the corner of Arson and Tower Direct Radiation Q T53 NE/55o 0.2 mi Site boundary fence east of South Cooling Tower Direct Radiation Q T54 S/1890 0.3 mi Pole, next to Fermi 2 Visitors Center Direct Radiation Q T55 WSW/2510 3.3 mi First pole east of Frenchtown Fire Station entrance, across from Sodt Direct Radiation Q Elementary School T56 WSW/2550 4.9 mi Pole, entrance to Jefferson Middle School on Stony Creek Rd. Direct Radiation Q T57 W/2600 2.7 mi Pole, north side of Williams Rd. across from Jefferson High School Direct Radiation Q entrance T58 WSW/2490 4,9 mi Pole, west of Hurd Elementary School Marquee Direct Radiation Q T59 NW/3250 2.6 mi Pole, north of St. Charles Church entrance on Dixie Hwy. Direct Radiation Q T60 NNW/3410 2.5 mi 1st pole north of North Elementary School entrance on Dixie Hwy. Direct Radiation Q FERMI 2 ODICM - T.RM VOLUME 11 10-8 Rev. 13 1

TABLE 10.0-1 Radiological Environmental Monitoring Program, Fermi 2 Sample Locations and Associated Media Direct Radiation Station Meteorological Distance from Number Sector/Azimuth Reactor (Approx.) Description Media Frequency Direction T61 W/2680 10.1 mi Pole, SW Corner of Stewart and Raisinville Rds Direct Radiation Q T62 SW/232o 9.7 mi Pole, NW Corner of Albain and Hull Rds. Direct Radiation Q T63 WSW/2450 9.6 mi Pole, Corner of Dunbar and Telegraph Rds. Direct Radiation Q T64 WNW/286 0 0.2 mi W of switchgear yard on PAF Direct Radiation Q T65 NW/3220 0.1 mi PAF switchgear yard area NW of RHR complex Direct Radiation Q 0

T66 NE/50 0.1 mi Behind Bldg. 42 on PAF Direct Radiation Q T67 NNW/3380 0.2 mi Site boundary fence W of S cooling tower Direct Radiation Q FERMI 2 ODCM - TRM VOLUME II 10-9 Rev. 13 1

TABLE 10.0-1 Radiological Environmental Monitoring Program, Fermi 2 Sample Locations and Associated Media Fish and Sediment Station Meteorologiical Distance from Number Sector/Azim uth Reactor (Approx.) Description Media Frequency Direction SEDIMENTS S-1 SSE1165 0 0.9 mi Pointe Aux Peaux, Shoreline to 500 ft. offshore sighting directly to Sediment SA Land Base Water Tower S-2 E/81 0 0.2 mi Fermi 2 Discharge, approx. 200 ft. offshore Sediment SA S-3 NE/39 0 1.1 mi Estral Beach, approx. 200 ft. offshore, off North shoreline where Sediment SA Swan Creek and Lake Erie meet S-4 WSW/24 10 3.0 mi indian Trails Community Beach Sediment SA S-5 NNE/200 11.7 mi DECo's Trenton Channel Power Plant intake area (Control) Sediment SA FISH F-1 NNE/310 9.5 mi Celeron Island (Control) Fish SA F-2 E/860 0.4 mi Fermi 2 Discharge (Approx. 1200 ft. offshore) Fish SA F-3 SW12270 3.5 mi Breast Bay Area (Control) Fish SA FERMI 2 ODCM - TRM VOLUME II 10-10 Rev. 13

TABLE 10.0;1 Radiological Environmental Monitoring Program, Fermi 2 Sample Locations and Associated Media Milk/Grass Station Meteorological Distance from Number Sector/Azimuth Reactor (Approx.) Description Media Frequency Direction 0

M-2 NW/319 5.4 mi Reaume Farm -2705 E. Labo Milk M-SM M-B WNWI289 0 9.9 mi Calder Dairy - 9334 Finzel Rd. Milk M-SM FERMI 2 ODCM - TRM VOLUME II 10-11 Rev. 13

TABLE 10.0-1 Radiological Environmental Monitoring Program, Fermi 2 Sample Locations and Associated Media Water Station Meteorological Distance from Number Sector/Azimuth Reactor (Approx.) Description Media Frequency Direction DRINKING WATER DW-1 S/1740 1.1 mi Monroe Water Station N Side of Pointe Aux Peaux 1/2 Block W of Drinking Water M Long Rd.

DW-2 N/80 18.5 mi Detroit Water Station, 14700 Moran Rd. Allen Park (Control) Drinking Water M SURFACE WATER 11.7 mi DECo's Trenton Channel Power Plant Intake Structure (Screenhouse SW-2 NNE/20 0 Surface Water M

1) (Control)

SW-3 SSE/1600 0.2 mi DECo's Fermi 2 General Service Water Intake Structure Surface Water M SITE WELLS GW-1 S/1750 0.4 mi Approx. 100 ft. W of Lake Erie, EF-1 Parking lot Groundwater near Groundwater Q gas fired peakers GW-2 SSW/2080 1.0 mi 4 ft. S of Pointe Aux Peaux (PAP) Rd. Fence 427 ft. W of where PAP Groundwater Q

crosses over Stony Point's Western Dike GW-3 SW/226 0 1.0 mi 143 ft. W of PAP Rd. Gate, 62 ft, N of PAP Rd. Fence Groundwater GW-4 WNW/299 0 0.6 mi 42 ft. S of Langton Rd., 8 ft. E of Toll Rd. Fence Groundwater Q_

FERMI 20DCM - TRM VOLUME II 10-12 Rev. 13

TABLE 10.0-1 Radiological Environmental Monitoring Program, Fermi 2 Sample Locations and Associated Media Air Particulate Air Iodine API-1 NEW390 1.4 mi Estral Beach Pole on Lakeshore, 18 Poles S of Lakeview (Nearest Radioiodine W Community with highest X IQ) Priuae API-2 NNW/3370 0.6 mi Site Boundary and Toll Road, on Site Fence by T-4 Radioiodine W Particulates W API-3 NW/313° 0.6 mi - Doy Boundary Site R. (ontol)Particulates

.and Toll Road, on Site Fence by T-5 Radioiodine W W

SParticulates W API-4 W12700 14.0 mi Pole, at Michigan Gas substation on N. Custer Rd[, 0.66 miles W of Radioiodine W

Doty Rd, (control) Particulates W API-5 ; S/1880 !1.2 mi Pole, N corner of Pointe Aux Peaux and Dewey Rd. Radioiodine W SParticulates W Note: iage content was, last changed with ODCM Revision 16.

FERMI 2 ODCM -TRM VOLUME II 10-13 Rev. 18

TABLE 10.0-1 Radiological Environmental Monitoring Program, Fermi 2 Sample Locations and Associated Media Food Products FP-1 NNE/21 0 3.8 mi 9501 Turnpike Highway Food Products M (when available)

I FP-9 W1261 0 10.9 mi 4074 North Custer Road Food Products M (when available)

Note: 'age content was last changed with ODCM Revision 16.

FERMI 2 ODCM - TRM VOLUME II 10-14 12/07 i Rev. 18

TABLE 10.0-1 Radiological Environmental Monitoring Program, Fermi 2 Sample Locations and Associated Media Land Use Census Closest Residences

___1NE 1mi

___ NNE 1.0mi N 1.1 mi NNW 1.1 mi NW 1.1 mi WNW 0.7 mi W 1.2 mi I

_ WSW\ 1.6 mi

___ SW 1.3 mi SSW 1.1 mi S 1.0 mi Merc Oct I I - I =I(I, Fri*

Lake Erie END OF SECTION 10.0 Note: Dage content was last changed with ODCM Revision 16.

FERMý 2 ODCM - TRM VOLUME II it /07 10-15 Rev. 18

NRC-08-0031, Technical Requirements Manual Offsite Dose Calculation Manual Volume II

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NRC-08-0031, Technical Requirements Manual Offsite Dose Calculation Manual Volume II

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