Text

Supplement to 2007 Annual Radioactive Effluent Release Report
	ML081640322
Person / Time
Site:	Turkey Point
Issue date:	05/30/2008
From:	Jefferson W; Florida Power & Light Co
To:	; Document Control Desk, Office of Nuclear Reactor Regulation
References
	L-2008-130
	Download: ML081640322 (213)
	v • d • e

0 FPL.

POWERING TODAY.

MAY 3 0 2008 L-2008-130 EMPOWERING TOMORROW.

U. S. Nuclear Regulatory Commission Attn: Document Control Desk Washington, D.C. 20555-00001 Re: Turkey Point Units 3 and 4 Docket Nos. 50-250 and 50-251 Supplement to 2007 Annual Radioactive Effluent Release Report The purpose of this letter is to supplement the 2007 Annual Radioactive Effluent Release Report, submitted to NRC by FPL letter L-2008-061, and dated March 20, 2008, by providing a copy of the entire Offsite Dose Calculation Manual (ODCM) to comply with Technical Specification (TS) 6.14.2.c. requirements. The revised ODCM is enclosed.

It was identified that although the 2007Annual Radioactive Effluent Release Report provided the ODCM revisions in Attachment A, it omitted the submittal of the entire ODCM as required per Technical Specifications 6.14.2.c.

Should there be any questions or comments regarding this information, please contact Olga Hanek, Licensing Manager at (305) 246-6607.

Very truly yours, Vice President Turkey Point Nuclear Plant SM Enclosure cc: Regional Administrator, Region II, USNRC Senior Resident Inspector, USNRC, Turkey Point Plant D7KY78 A-005 an FPL Group company k tZ4ý

Enclosure to L-2008-130 Revised ODCM Supplement to L-2008-061 2007 Annual Radioactive Effluent Release Report

OFFSITE DOSE CALCULATION MANUAL FOR GASEOUS AND LIQUID EFFLUENTS FROM THE TURKEY POINT PLANT UNITS 3 AND 4 REVISION 14 CHANGE DATED 6/4/07 Florida Power and Light Company

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL LIST OF EFFECTIVE PAGES Offsite Dose Calculation Manual Page Revision Date Page Revision Date Page Revision Date i 06/04/07 2-13 11/22/02 3-15 06/04/07 ii 06/04/07 2-14 06/04/07 3-16 06/04/07 iii 06/04/07 2-15 11/22/02 3-17 06/04/07 iv 06/04/07 2-16 11/22/02 3-18 06/04/07 v 11/22/02 2-17 11/22/02 3-19 06/04/07 vi 06/04/07 2-18 11/22/02 3-20 06/04/07 vii 11/22/02 2-19 11/22/02 3-21 06/04/07 viii 11/22/02 2-20 11/22/02 3 - - 11/22/02,--.

1-1 11/22/02 2-21 11/22/02 3-23 11/22/02 1-2 11/22/02 2-22 11/22/02 3-24 11/22/02 1-3 11/22/02 2-23 11/22/02 3-25 11/22/02 1-4 06/04/07 2-24 11/22/02 3-26 11/22/02 1-5 06/04/07 2-25 11/22/02 3-27 11/22/02 1-6 11/22/02 2-26 11/22/02 3-28 06/04/07 1-7 06/04/07 2-27 11/22/02 3-29 11/22/02 1-8 06/04/07 2-28 11/22/02 3-30 11/22/02-1-9 06/04/07 2-29 11/22/02 3-31 06/04/07 1-10 06/04/07 2-30 11/22/02 3-32 11/22/02 1-11 11/22/02 2-31 11/22/02 3-33 11/22/02 -

1-12 11/22/02 2-32 11/22/02 3-34 11/22/02 .

1-13 11/22/02 2-33 11/22/02 3-35 11/22/02 1-14 11/22/02 2-34 11/22/02 3-36 11/22/02 1-15 11/22/02 3-1 11/22/02 3-37 11/22/02 1-16 06/04/07 3-2 11/22/02 3-38 11/22/02 2-1 11/22/02 3-3 06/04/07 3-39 11/22/02 2-2 11/22/02 3-4 11/22/02 3-40 11/22/02 2-3 11/22/02 3-5 06/04/07 3-41 11/22/02 2-4 11/22/02 3-6 11/22/02 3-42 11/22/02 2-5 11/22/02 3-7 11/22/02 3-43 11/22/02 2-6 11/22/02 3-8 11/22/02 3-44 11/22/02 2-7 11/22/02 3-9 11/22/02 3-45 11/22/02 2-8 11/22/02 3-10 11/22/02 3-46 11/22/02 2-9 11/22/02 3-11 06/04/07 3-47 11/22/02 2-10 11/22/02 3-12 06/04/07 3-48 11/22/02 2-11 11/22/02 3-13 06/04/07 3-49 11/22/02 2-12 11/22/02 3-14 06/04/07 3-50 11/22/02 6/4/07 Rev 13

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL LIST OF EFFECTIVE PAGES Offsite Dose Calculation Manual Page Revision Date Page Revision Date Page Revision Date 3-51 11/22/02 5-13 11/22/02 3B-18 11/22/02 3-52 11/22/02 5-14-. 11/22/02 3B-19 11/22/02 3-53 11/22/02 5-15 11/22/02 3B-20 11/22/02 3-54 11/22/02 5-16 11/22/02 31B-21 11/22/02 3-55 11/22/02 5-17 11/22/02 31B-22 11/22/02 3-56 11/22/02 5-18 11/22/02 3B-23 11/22/02 3-57 11/22/02 5-19 11/22/02 3B-24 11/22/02 3-58 11/22/02 5-20 11/22/02 31B-25 11/22/02 3-59 .11/22/02 5-21 11/22/02 31B-26 11/22/02 3-60 11/22/02 5-22 11/22/02 3B-27 11/22/02 3-61 11/22/02 5-23 11/22/02 31B-28 11/22/02 3-62 11/22/02 5-24 11/22/02 3B-29 11/22/02 3-63 11/22/02 2A-1 11/22/02 3B-30 11/22/02 3-64 11/22/02 2A2 11/22/02 31B-31 11/22/02 3-65 11/22/02 2A3 11/22/02 3B-32 11/22/02 3-67 11/22/02 2A-4 11/22/02 3B-33 11/22/02 3-68 11/22/02 3A-1 11/22/02 3B-34 11/22/02 3-69 11/22/02 3A-2 11/22/02 3B-35 11/22/02 3-70 11/22/02 3A-3 11/22/02 3B-36 11/22/02 4-1 11/22/02 3A-4 11/22/02 3B-37 11/22/02 4-2 11/22/02 3A-5 11/22/02 3B-38 11/22/02 4-3 11/22/02 3A-6 11/22/02 3B-39 11/22/02 4-4 11/22/02 3A-7 11/22/02 3B-40 11/22/02 4-5 11/22/02 3B-1 11/22/02 3B-41 11/22/02 4-6 11/22/02 3B-2 11/22/02 3B-42 11/22/02 4-7 11/22/02 3B-3 11/22/02 3B-43 11/22/02 4-8 11/22/02 3B-4 11/22/02 3B-44 11/22/02 4-9 11/22/02 3B-5 11/22/02 3B-45 11/22/02 5-1 11/22/02 3B-6 11/22/02 3B-46 11/22/02 5-2 11/22/02 3B-7 11/22/02 3B-47 11/22/02 5-3 11/22/02 3B-8 11/22/02 3B-48 11/22/02 5-4 11/22/02 3B-9 11/22/02 3B-49 11/22/02 5-5 11/22/02 3B-10 11/22/02 3B-50 11/22/02 5-6 11/22/02 3B-11 11/22/02 3B-51 11/22/02 5-7 11/22/02 3B-12 11/22/02 3B-52 11/22/02 5-8 11/22/02 3B-13 11/22/02 3B-53 11/22/02 5-9 06/04/07 3B-14 11/22/02 3B-54 11/22/02 5-10 11/22/02 3B-15 11/22/02 3B-55 11/22/02 5-11 11/22/02 3B-16 11/22/02 3B-56 11/22/02 5-12 11/22/02 3B-17 11/22/02 ii 6/4/07 Rev 12

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL LIST OF EFFECTIVE PAGES Offsite Dose Calculation Manual PAGE DATE 3B-57 11/22/02 3C-1 11/22/02 3C-2 11/22/02 3C-3 11/22/02 5A-1 11/22/02 5A-2 11/22/02 5A-3 06/04/07 5A-4 11/22/02 5B-1 06/04/07 5B-2 06/04/07 iii 11/22/02 Rev 11

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL TABLE OF CONTENTS Introduction vii 1.0 Administrative Controls Control 1.1 ODCM Review and Approval .................................................... 1-1 Control 1.2 Major Changes to Liquid, Gaseous and Solid Radwaste Treatment Systems ................................................... 1- 2 Control 1.3 Annual Radioactive Effluent Release Report ............................ 1- 3 C.ontrol 1.4 Annual Radiological Environmental Operating Report ............... 1- 5 C ontrol 1.5 D efinitions .................................................................................. 1- 6 Control 1.6 Applicability of Controls .............................................................. 1 - 14 Control'1.7 Surveillance Requirements ........................................................ 1 - 15

t. C ontrol_1 8 References ..................................................................... 1 - 16 Figure 115-1 S ite A rea M ap ........................................................................... 1 - 12 Figure -1.5 P lant A rea Map .......................................................................... 1 - 13 2.0 Radioactive Liquid Effluents Control 2.1 Liquid Effluent Monitoring Instrumentation, Operability and Alarm/Trip Setpoints ........................................... 2- 5 Control 2.2 Concentrations in Radioactive Effluents .................... 2 - 14 Control 2.3 Dose From Radioactive Liquid Effluent ....................................... 2 - 24 Control 2.4 Liquid Radwaste Treatment System .......................................... 2 - 31 Figure 2 - 1 Radioactive Liquid Waste ........................................................... 2-4 Appendix 2A Radioactive Liquid Effluents Pathway Dose Transfer Factors ............................................................... 2A - 1 iv 6/4/07 Rev 11

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL TABLE OF CONTENTS (continued) 3.0 Radioactive Gaseous Effluents Control 3.1 Radioactive Gaseous Effluent Monitoring Instrumentation; Operability and Alarm/Trip Setpoints .......................................... 3-10 Control 3.2 Dose Rate From Radioactive Gaseous Effluents ....................... 3 - 27 Control 3.3 Air Dose From Noble G ases ...................................................... 3 - 45 Control 3.4 Dose Iodine-131, Iodine-133, Tritium, and

- Radioactive Material in Particulate Form ....................................

3 - 53 Control 3.5 Gaseous Radwaste Treatment System ...................................... 3 - 68 Figure 3 - 1 Radioactive Gaseous Waste ...................................................... 3-8 Figure 3 - 2 Locations of Airborne Effluent Dose Calculations ...................... 3-9 Appendix 3A Reference Meteorology Annual Average Atm ospheric Dispersion Factors ................................................ 3A- 1 Appendix 3B Pathway-Dose Transfer Factors .............................................

3C - 1 Appendix 3C Technical Bases for Aeff and TG 131 . . . . . . . . . . . . . . . . .. . .

4.0 Total Dose Control 4.1 Limits of Total Dose to Members of the Public ............................ 4-1 v 11/22/02 Rev 11

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL TABLE OF CONTENTS (continued 5.0 Radiological Environmental Monitoring Program

- Control 5.1 Conduct of Sampling and Analysis .......... .. ........................ 5 C ontrol 5.2 Land Use C ensus ........................................................................ 5 - 19 Control 5.3 Interlaboratory Comparison Program .......................................... 5 - 21

.- 'Figure 5.1-1 Near Site Sampling Locations ........................... 5- 17 Figure 5.1-2 Distant REMP Sampling Locations............................................. 5 - 18 Appendix 5A Turkey Point Supplemental Radiological Environmental Monitoring Program ....................... 5A- 1 Appendix 5B Turkey Point Groundwater Sampling Program to support the INDUSTRY INITIATIVE on G roundw ater Protection ...................................................... 5B - 1 vi 6/4/07 Rev 12

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL INTRODUCTION PURPOSE This manual describes methods which are acceptable for calculating radioactivity concentrations in the environment and potential offsite doses associated with liquid and gaseous effluents from the Turkey Point Nuclear Units. These calculations are performed to satisfy Technical Specifications and to ensure that the radioactive dose or dose commitment to any member of the public is not exceeded.

_ The radioactivity concentration calculations and dose estimates in this manual are used to

.. demonstrate compliance with the Technical Specifications required by_10 CFR 50.36. The methods used are acceptable for demonstrating operational compliance with 10 CFR 20.1302, 10CFR50 Appendix I, and 40CFR190. Only the doses attributable to Turkey Point Units 3 and 4 are determined in demonstrating compliance with 40CFR190 since there are no other nuclear facilities within 50 miles of the plant. Monthly calculations are performed to verify that potential offsite releases do not exceed Technical Specifications and to provide guidance for the management of radioactive effluents. The dose receptor is described such that the exposure of any member of the public is not likely to be substantially underestimated.

Quarterly and annual calculations of committed dose are also performed to verify compliance with regulatory limits of offsite dose. For these calculations, the dose receptor is chosen on the basis of applicable exposure pathways identified in a land use survey and the maximum ground level atmospheric dispersion factor (X/Q) at a residence, or on the basis of more conservative conditions such that the dose to any resident near the plant is not likely to be underestimated.

The radioactive effluent controls set forth in this ODCM are designed to allow operational flexibility but still maintain releases and doses "as low as is reasonably achievable"; that is, within the objectives of Appendix 1, 10 CFR Part 50 and comply with the limits in 10 CFR 20.1302.

The methods specified in the OFFSITE DOSE CALCULATION MANUAL (ODCM) for calculating doses due to planned or actual releases are consistent with the guidance and methods 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.

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.

vii 11/22/02 Rev 11

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL INTRODUCTION, (continued)

Regulatory Guide 1.113, "Estimating Aquatic Dispersion of Effluents from Accidental and Routine Reactor Releases for the Purpose of Implementing Appendix I," April 1977.

The required detection capabilities for radioactive materials in liquid and gaseous waste samples are tabulated in terms of the lower limits of detection (LDD's). Detailed discussion of the LLD and other detection limits, can be found in Currie, L. A., "Lower Limit of Detection:. Definition and Elaboration of a Proposed Position for Radiological Effluent and Environmental Measurements,"

NUREG/CR-4077 (September 1984), in HASL Procedures Manual, HASL300 and in Hartwell, J. K.,

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

viii 11/22/02 Rev 11

SECTION 1' ADMINISTRATIVE CONTROLS

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 1.0 ADMINISTRATIVE CONTROLS CONTROL 1.1 : ODCM REVIEW AND APPROVAL 1.1.1 Responsibility for Review The Chemistry Department Supervisor or designee shall perform a review of the ODCM annually.

1.1.2Documentation of Reviews Following the performance of the annual review required by Section 1.1.1, the individual performing the review shall submit a report for PNSC approval. This report should contain the following information:

1. A copy of any requested changes to the ODCM.

2. Information necessary to support the rationale for the requested changes.

3. A determination that the requested changes will not reduce the accuracy or reliability of dose calculations or setpoint determinations.

4. If no changes are being requested, no actions are required.

-1.1.3lnstitution of Changes Changes to the ODCM shall become effective upon review and approval by the Plant General Manager, (PGM).

_1.1.4Submittal of Changes Changes to the ODCM and any supporting documentation shall be submitted to the NRC in the Annual Radioactive Effluent Release Report for the period in which the changes were made effective. This submittal, per Control 1.3, shall contain the following information:

1. Sufficiently detailed information to totally support the rationale for the changes(s) without benefit of additional or supplemental information.

2. Information submitted should consist of a package of those pages of the ODCM to be changed with each page numbered, dated and containing the revision number, together with appropriate analyses or evaluations justifying the change(s)

3. A determination that the change(s) will not reduce the accuracy or reliability of dose calculations or setpoint determinations; and

4. Documentation of the fact that the change(s) has been reviewed and found acceptable by the PGM.

1-1 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 1.0 ADMINISTRATIVE CONTROLS CONTROL 1.2: MAJOR CHANGES TO LIQUID, GASEOUS AND SOLID RADWASTE TREATMENT SYSTEMS*

Licensee-initiated major changes to the Liquid, Gaseous, and Solid Radwaste Treatment Systems:

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 Plant General Manager. 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 supplemental information; (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 change is 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 PGM.

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

Licensees may choose to submit the information called for in this Control as part of the annual FSAR update.

1-2 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 1.0 ADMINISTRATIVE CONTROLS CONTROL 1.3: ANNUAL RADIOACTIVE EFFLUENT RELEASE REPORT

An Annual Radioactive Effluent Release Report covering the operation of the unit during the previous 12 months of operation shall be submitted by April 1 of each year and shall include:

a. 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.

For solid wastes, the format for Table 3 in Appendix B shall be supplemented with three additional categories: class of solid wastes (as defined by 10 CFR Part 61), type of container (e.g., strong tight package, Type A, Type B) and solidification agent or absorbent (e.g., cement).

b. 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 magnetic tape 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 stability.** 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 1.5-1) 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 meteorological conditions concurrent with the time of release of radioactive materials in gaseous effluents, as determined by sampling frequency and measurement, shall be used for determining the gaseous pathway doses. Approximate and conservative methods may be used in lieu of actual meteorological measurements. The assessment of radiation doses shall be performed in accordance with the methodology and parameters in this OFFSITE DOSE CALCULATION MANUAL (ODCM).

1-3 11/22/02

TURKEY POINT UNIT 3 & 4OFFSITE DOSE CALCULATION MANUAL 1.0 ADMINISTRATIVE CONTROLS CONTROL 1.3: Annual Radioactive Effluent Release Report *, (continued)

c. An assessment of radiation doses to the likely most exposed MEMBER OF THE PUBLIC from reactor releases from the previous calendar year 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." Acceptable methods for calculating the dose contribution from liquid and gaseous effluents are given in Regulatory Guide 1.109, Revision 1, October 1977.

d. 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.

e. Any changes made during the reporting period to the OFFSITE DOSE CALCULATION MANUAL (ODCM), pursuant to Technical Specification 6.14, as well as any major change to Liquid, Gaseous, or Solid Radwaste Treatment Systems pursuant to Control 1.2. It shall also include a listing of new locations for dose calculations and/or environmental monitoring identified by the Land Use Census pursuant to Control 5.2.

f. An explanation, if applicable, as to why the inoperability of liquid or gaseous effluent monitoring instrumentation was not corrected within the time specified in Control 2.1 or 3.1, respectively; and description of the events leading to liquid holdup tanks or gas storage tanks exceeding the limits of Technical Specification 3.7.9.

g. Beginning with the Report that is due April 1, 2007, the Annual Radioactive Effluent Release Reports shall include the following information for the previous year:

i. A listing description of all leaks or spills that have been communicated to State and Local Officials in accordance with the INDUSTRY INITIATIVE (Nuclear Policy NP-922).

ii. Groundwater sample results that have been taken in support of the INDUSTRY INITIATIVE (Nuclear Policy NP-922), unless they are from locations that are described in the Radiological Environmental Monitoring Program (REMP) and will therefore be reported in the Annual Radiological Environmental Operating Report. See Appendix 5B for details.

A single submittal may be made for a multiple 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.

- 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.

1-4 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 1.0 ADMINISTRATIVE CONTROLS CONTROL 1.4 ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT"*

Routine Annual Radiological Environmental Operating Reports covering the operation of the Unit during the -previous calendar year shall be submitted prior to May 15 of the following year and shall include :

a. Summaries, interpretations, and an analysis of trends of the results of the radiological environmental surveillance activities for the report period, including a comparison with preoperational studies, with operational controls, as appropriate, 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 the Land Use Census required by Control 5.2

b. The results of analysis of all radiological environmental samples and of all environmental radiation measurements taken during the period pursuant to the locations specified in the table and figures in Control 5.1, 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. The missing data shall be submitted as soon as possible in a supplementary report.

c. A summary description of the Radiological Environmental Monitoring Program; at least two legible maps ** covering all sampling locations keyed to a table giving distances and directions from the centerline of one reactor; the results of licensee participation in the Interlaboratory Comparison Program and the corrective action taken if the specified program is not being performed as required by Control 5.3; reasons for not conducting the Radiological Environmental Monitoring Program as required by Control 5.1, and discussion of all deviations from the sampling schedule of Table 5.1 -1;- discussion of environmental sample measurements that exceed the reporting levels of Table 5.1-2 but are not the result of plant effluents, pursuant to ACTION b. of Control 5.1; and discussion of all analyses in which the LLD required by Table 5.1-3 was not achievable.

d. Results from the Turkey Point Groundwater Sampling Program for the samples and locations in Appendix 5B.

A single submittal may be made for a multiple unit station.

- One map shall cover stations near the SITE BOUNDARY; a second shall include the more distant stations.

1-5 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 1.0 ADMINISTRATIVE CONTROLS 1.5 DEFINITIONS The defined -terms of this section appear in capitalized type and are applicable throughout the Offsite Dose Calculation Manual.

ACTION 1.5.1 An ACTION shall be that part of a control which prescribes remedial measures required under designated conditions.

ANALOG CHANNEL OPERATIONAL TEST 1.5.2 An ANALOG CHANNEL OPERATIONAL TEST shall be the injection of a simulated signal into the channel as close to the sensor as practicable to verify OPERABILITY of alarm, interlock and/or trip functions. The ANALOG CHANNEL OPERATIONAL TEST shall include adjustments, as necessary, of the alarm, interlock and/or Trip Setpoints such that the setpoints are within the required range and accuracy CHANNEL CALLIBRATION 1.5.3 A CHANNEL CALIBRATION shall be the adjustment, as necessary, of the channel such that it responds within the required range and accuracy to known values of input. The CHANNEL CALIBRATION shall encompass the entire channel including the sensors and alarm, interlock and/or trip functions and may be performed by any series of sequential, overlapping, or total channel steps such that the entire channel is calibrated.

CHANNEL CHECK 1.5.4 A CHANNEL CHECK shall be the qualitative assessment of channel behavior during operation by observation. 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.

1-6 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 1.0 ADMINISTRATIVE CONTROLS 1.5 DEFINITIONS (continued)

DOSE EQUIVALENT 1-131 1.5.5 DOSE EQUIVALENT 1-131 shall be that concentration of 1-131 (microCurie/gram) which alone would produce the same thyroid dose as the quantity and isotopic mixture of 1-131, 1-132, 1-133, 1-134, and 1-135 actually present. The thyroid dose conversion factors used for this calculation shall be those listed in Table III of TID-14844, "Calculation of Distance Factors for Power and Test Reactor Sites" or Table E-7 of NRC Regulatory Guide 1.109, Revision 1, October 1977.

FREQUENCY NOTATION 1.5.6 The FREQUENCY NOTATION specified for the performance of Surveillance Requirements shall correspond to the intervals defined in Table 1.5-1 GAS DECAY TANK SYSTEM 1.5.7 A GAS DECAY TANK SYSTEM shall be any system designed and installed to reduce radioactive gaseous effluents by collecting Reactor Coolant System off gases from the Reactor Coolant System and providing for delay or holdup for the purpose of reducing the total radioactivity prior to release to the environment.

INDUSTRY INITIATIVE 1.5.8Nuclear Energy Institute Initiative on Managing Situations Involving Inadvertent Radiological Releases into Groundwater (The INDUSTRY INITIATIVE has been adopted through Nuclear Policy, NP-922).

INITIAL CALIBRATION 1.5.9 INITIAL CALIBRATION - An INITIAL CALIBRATION is the determination of the detector sensitivity when the detector is exposed in a known geometry to radiation from sources of known energies and activity levels traceable to National Institute of Standards & Technology (NIST). The vendor usually performs this calibration.

Furthermore, subsequent CHANNEL CALIBRATIONS should include the use of a TRACEABLE SOURCE positioned in a reproducible geometry with respect to the sensor whose effect on the system was established at the time of the initial calibration. This CHANNEL CALIBRATION will establish the dynamic capabilities of a detector, electronics and power supplies in such a way as to ensure that the detector will perform its basic task of sensing radiation at the predetermined minimum detectable concentration based on the Initial Calibration.

MEMBER(S) OF THE PUBLIC 1-7 6/4/07

TURKEY POINT UNIT 3 & 4-OFFSITE DOSE CALCULATION MANUAL 1.0 ADMINISTRATIVE CONTROLS 1.5.10 MEMBER(S) OF THE PUBLIC shall mean any individual except when that individual is receiving an occupational dose.

1-7 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 1.0 ADMINISTRATIVE CONTROLS 1.5 DEFINITIONS (continued)

OFFSITE DOSE CALCULATION MANUAL 1.5.11 The OFFSITE DOSE CALCULATION MANUAL (ODCM) shall contain the methodology and parameters used in the calculation of offsite doses resulting from radioactive gaseous and liquid effluents, in the calculation of gaseous and liquid effluent monitoring Alarm/Trip setpoints, and in the conduct of the Environmental Radiological Monitoring Program. The ODCM shall also contain (1) the Radioactive Effluent Controls and Radiological Environmental Monitoring Programs required by Tech Spec Section 6.8.4 and (2) descriptions of the information that should be included in the Annual Radioactive Effluent Release Report and the Annual Radiological Environmental Operating Report required by Controls 1.3 and 1.4.

OPERABLE - OPERABILITY 1.5.12 A system, subsystem, train, component or device shall be OPERABLE or have OPERABILITY when it is capable of performing its'specified function(s), and when all necessary attendant instrumentation, controls, electrical power, cooling or seal water, lubrication or other auxiliary equipment that are required for the system, subsystem, train, component, or device to perform its function(s) are also capable of performing their related support function(s).

OPERATIONAL MODE - MODE 1.5.13 An OPERATIONAL MODE (i.e., MODE) shall correspond to any one inclusive combination of core reactivity condition, power level, and average reactor coolant temperature specified in Table 1.5-2 PROCESS CONTROL PROGRAM 1.5.14 The PROCESS CONTROL PROGRAM (PCP) shall contain the current formulas, sampling, analysis, tests, and determinations to be made to ensure that processing and packaging of solid radioactive wastes based on demonstrated processing of actual or simulated wet solid wastes will be accomplished in such a way as to assure compliance with 10 CFR Parts 20, 61, and 71 and Federal and State regulations, burial ground requirements, and other requirements governing the disposal of radioactive waste.

1-8 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 1.0 ADMINISTRATIVE CONTROLS 1.5 DEFINITIONS (continued)

PURGE - PURGING 1.5.15 PURGE or PURGING shall be any 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 1.5.16 RATED THERMAL POWER shall be a total reactor core heat transfer rate to the reactor coolant of 2300 MWt REPORTABLE EVENT 1.5.17 A REPORTABLE EVENT shall be any of those conditions specified in Section 50.73 of 10 CFR Part 50.

SAMPLING EVALUATION 1.5.18 A SAMPLING EVOLUTION is the exchange of iodine cartridge or particulate filter or the attachment of a sample rig to obtain a noble gas or tritum sample.

SITE BOUNDARY 1.5.19 The SITE BOUNDARY shall mean that line beyond which the land or property is not owned, leased, or otherwise controlled by the licensee, see figure 1.5 - 1.

SOURCE CHECK 1.5.20 A SOURCE CHECK shall be the qualitative assessment of channel response when the channel sensor is exposed to a source of increased radioactivity.

THERMAL POWER 1.5.21 THERMAL POWER shall be the total reactor core heat transfer rate to the reactor coolant.

TRACEABLE SOURCE 1.5.22 TRACEABLE SOURCE - Radiation sources that are related not only to the reference sources that were used for the INITIAL CALIBRATION but also certified by the National Institute of Standards & Technology (NIST). These transfer sources will calibrate the detector by positioning it in a reproducible geometry as prescribed by the INITIAL CALIBRATION.

UNRESTRICTED AREA 1.5.23 An UNRESTRICTED AREA shall mean an area, access to which is neither limited nor controlled by the licensee.

1-9 6/4/07

TURKEY POINT UNIT 3 &_4 OFFSITE DOSE CALCULATION MANUAL 1.0 ADMINISTRATIVE CONTROLS 1.5 DEFINITIONS (continued)

VENTILATION EXHAUST TREATMENT SYSTEM 1.5.24 A VENTILATION EXHAUST TREATMENT SYSTEM shall be any system designed and installed to reduce gaseous radioactive iodine or radioactive material in particulate form in effluents by passing ventilation or vent exhaust gases through charcoal absorbers and/or HEPA filters for the purpose of removing iodine 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 Features Atmospheric Cleanup Systems are not considered to be VENTILATION EXHAUST TREATMENT SYSTEM components.

VENTING 1.5.25 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.

TABLE 1.5-1 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 7days.

M At least once per 31 days.

Q At least once per 92 days.

SA At least once per 184 days.

R At least once per 18 months.

S/U Prior to each reactor startup.

NA Not applicable.

P Completed prior to each batch release.

1-10 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 1.0 ADMINISTRATIVE CONTROLS 1.5 DEFINITIONS (continued)

TABLE 1.5-2 OPERATIONAL MODES REACTIVITY % RATED AVERAGE COOLANT MODE CONDITION, Kef THERMAL POWER TEMPERATURE

1. POWER OPERATION Ž0.99 >5% > 350 OF

2. STARTUP > 0.99 *5% > 350 OF

3. HOT STANDBY < 0.99 0 > 350 OF

4. HOT SHUTDOWN < 0.99 0 350 OF > Tavg

> 200 OF

5. COLD SHUTDOWN < 0.99 0 _200 OF

6. REFUELING < 0.95 0 _140 OF

Excluding decay heat.

- Fuel in the reactor vessel with the vessel head closure bolts less than fully tensioned or with the head removed.

1-11 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 1.0 ADMINISTRATIVE CONTROLS 1.5 DEFINITIONS (continued)

FIGURE 1.5- 1 SITE AREA MAP Meteorological tower Locations:

A. 10 Meter tower B. 60 Meter Tower 1-12 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 1.0 ADMINISTRATIVE CONTROLS FIGURE 1.5- 2 PLANT AREA MAP Gaseous Effluent Release Points Liquid Effluent Release Points

1. Plant Vent (Unit 4 Spent Fuel Pool Vent) 5. Effluent from Liquid Radwaste System

2. Unit 3 Spent Fuel Pool Vent 6. Effluent from Liquid Radwaste System

3. Unit 3 Air Ejector Vent 7. Unit 3 Steam Generator Blowdown

4. Unit 4 Air Ejector Vent 8. Unit 4 Steam Generator Blowdown

9. Storm Drain

10. Storm Drain

11. Storm Drain

12. Storm Drain NOTE: FIGURE SHOWS RELEASE POINTS. STRUCTURES ARE SHOWN FOR REFERENCE ONLY.

1-13 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 1.0 ADMINISTRATIVE CONTROLS 1.6 APPLICABILITY OF CONTROLS 1.6.1- Compliance with the Controls, contained in this 00CM, is required during the OPERATIONAL MODES or other conditions specified therein; except that upon failure to meet the Control, the associated ACTION requirements shall be met.

1.6.2 Noncompliance with a specification shall exist when the requirements of the Control and associated ACTION requirements are not met within the specified time intervals. If the Control is restored prior to expiration of the specified time intervals, completion of the ACTION requirements is not required.

1.6.3 When a Control is not met, except as provided in the associated ACTION requirements, within 1 hour1.157407e-5 days 2.777778e-4 hours 1.653439e-6 weeks 3.805e-7 months action shall be initiated to place the unit, as applicable, in

a. At least HOT STANDBY within the next 6 hours6.944444e-5 days 0.00167 hours 9.920635e-6 weeks 2.283e-6 months ,

b. At least HOT SHUTDOWN within the following 6 hours6.944444e-5 days 0.00167 hours 9.920635e-6 weeks 2.283e-6 months , and

c. At least COLD SHUTDOWN within the subsequent 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months .

Where corrective measures are completed that permit operation under the ACTION requirements, the action may be taken in accordance with the specified time limits as measured from the time of failure to meet the Control. Exceptions to these requirements are stated in the individual control.

This control is not applicable in MODES 5 or 6.

1.6.4 Entry into an OPERATIONAL MODE or other specified condition shall not be made when the conditions for the Control are not met and the associated ACTION requires a shutdown if they are not met within a specified time interval. Entry into an OPERATIONAL MODE or specified condition may be made in accordance with ACTION requirements when conformance to them permits continued operation of the facility for an unlimited period of time. This provision shall not prevent passage through or to OPERATIONAL MODES as required to comply with ACTION requirements. Exceptions to these requirements are stated in the individual controls.

1-14 11/22/02

TURKEY POINT-UNIT 3 & 4 OFFSITE DOSE CALCULATION[MANUAL 1.0 ADMINISTRATIVE CONTROLS 1.6 APPLICABILITY OFCONTROLS (continued) 1.6.5 Controls including the associated ACTION requirements shall apply to each unit individually unless otherwise indicated as follows:

a. Whenever the Control refers to systems or components which are shared by both units, the ACTION requirements will apply to both units simultaneously.

b. Whenever the Control applies to only one unit, this will be identified in the APPLICABILITY section of the Control: and

c. Whenever certain portions of a Control contain operating parameters, Setpoints, etc., which are different for each unit, this will be identified in parentheses, footnotes or body of the requirement.

1.6.6 Special reports shall be submitted to the Regional Administrator of the Regional Office of the NRC within the time period specified for each report as stated in the Controls within sections 2.0, 3.0, 4.0, or 5.0.

1.7 SURVEILLANCE REQUIREMENTS 1.7.1 Surveillance Requirements shall be met during the OPERATIONAL MODES or other conditions specified for individual Controls unless otherwise stated in an individual Surveillance Requirement.

1.7.2Each Surveillance Requirement shall be performed within the specified time interval with a maximum allowable extension not to exceed 25% of the surveillance interval.

1.7.3Failure to perform a Surveillance Requirement within the allowed surveillance interval, defined by Control 1.7.2, shall constitute noncompliance with the OPERABILITY requirements for a Control. The time limits of the ACTION requirements are applicable at the time it is identified that a Surveillance Requirement has not been performed. The ACTION requirements may be delayed for up to ,24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months to permit the completion of the surveillance when the allowable outage time limits of the ACTION requirements are less than 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months . Surveillance Requirements do not have to be performed on inoperable equipment.

1-15 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 1.0 ADMINISTRATIVE CONTROLS 1.7 SURVEILLANCE REQUIREMENTS (continued) 1.7.4Entry into an OPERATIONAL MODE or other specified condition shall not be made unless the Surveillance Requirement(s) associated with a Control has been performed within the stated surveillance interval or as otherwise specified. This provision shall not prevent passage through or to OPERATIONAL MODES as required to comply with ACTION requirements.

1.7.6Surveillance Requirements shall apply to each unit individually unless otherwise indicated as stated in Control 1.6.5 for individual controls or whenever certain portions of a control contain surveillance parameters different for each unit, which will be identified in parentheses, footnotes or body of the requirement.

1.8 REFERENCES

1. Condition Report (CR) 2005-17141, REMP QA Audit

2. PTN-ENG-SENS-05-049, Temporary Suspension of Continuous Monitoring via the Plant Vent and Unit 3 Spent Fuel Pool SPINGS for the performance of Required Maintenance.

3. PTN-ENG-SENS-06-048, The Calculation Developing the Iodine and Particulate Activity Compensation Factors for the Steam Jet Air Ejector Vent Monitors. This Engineering Evaluation is valid through 31 Dec. 2009.

4. Condition Report (CR) 2006-17093, Nuclear Energy Institute Industry Initiative on Managing Situations Involving Inadvertent Radiological Releases into Groundwater.

5. Condition Report (CR) 2006-17607, Sampling and Monitoring Groundwater at PTN.

6. Nuclear Policy NP-922, Managing Situations Involving Inadvertent Radological Releases into Groundwater. (Implements the INDUSTRY INITIATIVE).

1-16 6/4/07

SECTION 3

-- -RADIOACTIVE GASEOUS EFFLUENTS

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS OBJECTIVES & SYSTEM DESCRIPTION A. OBJECTIVES To provide calculational methodology needed to assure compliance with Technical Specifications which requires the following determinations and surveillances:

o Radionuclide concentrations in gaseous effluents o The dose rate due to radioactive gaseous effluents to areas at and beyond the site boundary are maintained within the limits of Control 3.2

- Total body dose rate from radioactive noble gases

- Skin dose rate from radioactive noble gases

- Organ dose rate from radioiodines, tritium, and particulates with half-lives greater than 8 days.

o Determine that the cumulative quarterly and annual doses per reactor at and beyond the site boundary, due to noble gases, are maintained below the limits of Control 3.3 at least once per 31 days.

0 Determine that the cumulative quarterly and annual doses per reactor at and beyond the site boundary from radioiodines, tritium, and particulates with half-lives greater than 8 days, are maintained below the limits of Control 3.4 at least once per

.-- .31 days.

o Project the doses due to gaseous releases from each unit at least once per 31 days when gaseous radwaste treatment systems are not being fully utilized.

B. BASES Radioactive gaseous effluents from Turkey Point Units 3 and 4 are released through four monitored release points; a common plant vent via a stack above the containment building

(-200 ft.), the Unit 3 spent fuel pit vent (-110 ft.), and the condenser air ejector vents (-51 ft.)

from each unit. Unmonitored radioactive airborne releases can also occur from the secondary steam systems of each unit if primary to secondary leakage is occurring. Accounting for the quantity of these unmonitored airborne releases, during periods of primary to secondary leakage, are performed using approved plant procedures and the most accurate means available. The effluent sources (refer to Figure 3-1) for each release point are tabulated in Table 3-1. The airborne releases from all these sources are treated as a mixed mode release from a single location for dose calculational purposes. They are considered a release from a single location due to their close proximity to one another relative to the distance to the site boundary.

3-1 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS OBJECTIVES & SYSTEM DESCRIPTION (continued)

B. BASIS, (continued)

A mixed mode release is selected since the majority of the releases made from the site fit the mixed mode release model as described in Regulatory Guide 1.111.

Compliance for beta and gamma dose limits at and beyond the site boundary for noble gas effluents is determined by assessing the dose rate and/or dose at the location where the minimum atmospheric dispersion occurs at the site boundary since the atmospheric dispersion will be higher at all other points off-site. This minimum dispersion occurs at the site boundary 1950 meters SSE of the plant where the dispersion factor is 5.8 x 10-7 sec/m 3 (see figure 3-2). This value was extrapolated from the tables in Appendix 3A and are periodically evaluated against actual meteorological data to ensure the validity of these tables.

The dose rate due to tritium, 1-131, 1-133, and radioactive particulates with half lives greater than 8 days at and beyond the site boundary is assessed by determining the dose rate to a hypothetical infant's thyroid via the inhalation pathway. The basis for this approach is NUREG-0133, "Preparation of Radiological Effluent Technical Specifications for Nuclear Power Plants" which states: the dose factors are dependent on the specific organ and on the age group. The infant is the most restrictive age group for the dose rate calculations and the most restrictive organ is the thyroid via either the inhalation or grass-cow-milk pathway. The dose from tritium, 1-131, 1-133, and particulate is calculated by assuming a cow on pasture 4.5 miles west of the plant unless there is a milk producer in a more conservative location. At that location the reference atmospheric deposition factor, D/Q, is equal to 5 x 1010 m2 (see figure 3-2). This value was extrapolated from the tables in Appendix 3A and are periodically evaluated against actual meteorological data to ensure the validity of these tables.

Sampling and analysis is performed as outlined in ODCM Table 3.2-1. Principal gamma emitters for batch gaseous effluents, from Gas Decay Tanks or Containment Purges, which are released via the Plant Vent are Noble Gases only. The iodines and particulates are collected on filter elements in the effluent monitors and are considered continuous releases. This method of accounting for iodine and particulate in batch releases is performed to preclude over accounting for these emissions since the ventilation path is the same as for continuous releases.

3-2 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS C. GASEOUS RADWASTE SYSTEM Radioactive and potentially radioactive gases from units 3 and 4 containment buildings, the auxiliary building, unit 4 spent fuel pit, radwaste building and laundry area are released via the monitored plant vent after passing through filter systems.

Radioactive waste gases from the primary systems (CVCS hold-up tanks) are stored in gas decay tanks to reduce activity levels by radioactive decay prior to release via the plant vent. The unit 3 spent fuel pit area is ventilated via its' own monitored vent after passing through a filtering system. The filtration systems for the Auxiliary Building, 3 & 4 Spent fuel Pit, the Radwaste Building, and the Laundry consist of a pre-filter and a HEPA filter. The Containment Buildings have roughing filters only.

The steam jet air ejectors from each unit are vented through monitored release pathways. Other steam losses concurrent with primary to secondary leakage are unmonitored and gaseous activity must be accounted for.

Radionuclides other than noble gases in the gaseous effluents are measured by the radioactive gaseous waste sampling and analysis program described in ODCM Table 3.2-1. Noble gas radionuclides are measured by continuous monitors in the four release points. The gaseous effluent streams monitoring points, and effluent discharge points are illustrated schematically in Figure 3-1.

The measured radionuclide concentrations in gaseous effluents from the plant are used for estimating offsite radionuclide concentrations and radiation doses.

Sampling and analyses are performed consistent with the requirements of ODCM Table 3.2-1.

The radioactive iodines and particulate radionuclides from continuous releases and batch releases ( Containment Purges and Gas Decay Tanks are released via the Plant Vent) are determined by charcoal and filter samples removed weekly from continuous sample trains installed at each release point (plant vent, condenser air ejectors and Unit 3 Spent Fuel Pit vent). Tritium activity is determined on monthly grab samples from the plant vent, condenser air ejector, and Unit 3 Spent Fuel Pit and by a grab sample from each containment purge.

The Condenser Air Ejector Exhaust pathway is not conducive to collection of iodine and particulate in that the pathway is not capable of isokinetic sampling. The exhaust flow rate varies, doesn't have an isokinetic nozzle and when condenser air in leakage is at very low flow rates emits puffs versus a constant flow rate.

Therefore the Steam Jet Air Ejector SPING will be sampling a mixture of Condenser off gas and the atmosphere, and not gathering a representative sample. To account for the inability to perform isokinetic sampling, compensation factors were developed to relate the estimated concentration of particulates and iodine to the concentration of noble gas emitted. Calculation dose, from this pathway, from particulates is performed assuming that all curies released are Co-60 and all iodine curies released is 1-131. No analysis for alpha or Sr-89 and Sr-90 will be performed.

The compensation factors developed using PTN-ENG-SENS-06-048, The Calculation Developing the Iodine and Particulate Activity Compensation Factors for the Steam Jet Air Ejector Vent Monitor,are valid until 31 Dec. 2009.

3-3 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS5 OBJECTIVES & SYSTEM DESCRIPTION (continued)

C. GASEOUS RADWASTE SYSTEM, (continued)

Additional grab samples are obtained and analyzed if the conditions identified in Notes 4,5,6 and 7 of ODCM Table 3.2-1 exist, i.e., tritium grab samples. once. per 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months when the refueling canal is flooded, tritium grab samples at least weekly from the spent fuel pool ventilation exhaust when spent fuel is inthe spent fuel pool, and sampling shall also be performed at least once per day for at least 7 days following each shutdown, startup or THERMAL POWER change exceeding 15% of RATED THERMAL POWER in one (1)hour and analyses shall be completed within 48 hours5.555556e-4 days 0.0133 hours 7.936508e-5 weeks 1.8264e-5 months of changing if both the following conditions are met:

(1) analysis shows that the DOSE EQUIVALENT 1-131 concentration in the primary coolant has increased by more than a factor of 3; AND (2) the noble gas activity monitor shows that the effluent activity has increased by more than a factor of 3.

Activities measured by these additional samples should be included in the cumulative dose calculations.

Noble gas activity released is measured by continuous noble gas monitors installed in each discharge point for release types listed in ODCM Table 3.2-1. The quantity of radioactive noble gas activity not accounted for by grab samples can be determined by integrating the release rate measurement from each effluent noble gas monitor.

3-4 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS OBJECTIVES & SYSTEM DESCRIPTION (continued)

C. GASEOUS RADWASTE SYSTEM, (continued)

The total measured radioactivity discharged via a stack or vent during a specific time period can be determined from the effluent monitors by:

Qj Nj

F

28317 hh where:

Qj = total measured gaseous radioactivity release via a stack or vent during counting interval j, (p.Ci)

Nj = counts accumulated during counting interval j, (counts = N(cpm) x t (min))

F = discharge rate of gaseous effluent stream, (ft3/min) 28317 = conversion constant, (cm 3 /ft3) h = effluent noble gas monitor calibration or counting rate response for noble gas gamma radiation, cpm p.Ci / cm3 During periods of primary to secondary leakage, the activity released through unmonitored pathways can be estimated using the following methods. Other more accurate methods may be used, when appropriate and with the proper level of management approval.

Qj= C x Fj xTj where:

C = The concentration of the individual isotope released.

Fj = The mass of unmonitored water and steam released through unmonitored pathways.

Fj = M, - (Mb + Ms)

M, = Mass rate of make up water Mb = Mass rate of blowdown Ms = Mass rate of steam from monitored sources Tj = Time interval for the period being quantified 3-5 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS OBJECTIVES & SYSTEM DESCRIPTION (continued)

C. GASEOUS RADWASTE SYSTEM, (continued)

The distribution of radioactive noble gases in a gaseous effluent stream is determined by gamma spectrum analysis of gas samples from that stream. Results of previous analyses may be averaged to obtain a representative distribution. When necessary, due to an uncontrolled release, samples from similar components in the same system can be used to determine a representative distribution.

Iffi represents the fraction of radionuclide i in a given effluent stream, based on the isotopic distribution of that stream, then the quantity of radionuclide i released in a given gaseous effluent stream during counting interval j is:

Qij = Qj

fi where:

Qij= quantity of radionuclide i released in a given gaseous effluent stream during counting interval j, (gCi) fi= the fraction of radionuclide i released in a given effluent stream In the event the radioactive noble gas distribution is not obtainable from sample(s) taken during the current period the distribution will be obtained from recent data if available.

Some gaseous effluents from both Units 3 and 4, whose sources are identified in Table 3-1, discharge in common through the plant vent. To assure that the effluents are within allowable limits per reactor, the measured release are allocated equally to both Units 3 and 4 for Gas Decay Tanks and all ventilation systems exhausting into the Plant Vent Stack. Unit 3 Spent Fuel Pit Vent, Containment purges, Steam Jet Air Ejector Vents, and Steam Generator Blowdown Vents are allocated to each unit as appropriate.

3-6 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 -RADIOACTIVE GASEOUS EFFLUENTS OBJECTIVES & SYSTEM DESCRIPTION (continued)

Table 3 - 1 Atmospheric Gaseous Release Points at the Turkey Point Units 3 and 4 Effluent Source Release Point Gas decay tanks Plant vent Radwaste Building Plant vent Auxiliary Building Plant vent Containment Purge Plant vent No. 4 spent fuel pit Plant vent No. 3 spent fuel pit Spent fuel pit vent Air ejectors Turbine deck Steam generator Blowdown vent blowdown 3-7 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS FIGURE 3 - 1 RADIOACTIVE GASEOUS WASTE Steam Steam Safeties Dumps Unit 3 Unit 4 Dumps Safeties int m

oank Coolants I i Pro F/ C Tana Exas I oo t Iaus Exh t ak uxm E

xhaus Sa t i Roughingm Exhaus h fier*

TonY1 reGal h..a Tank Sel6)hus de A n ir BOuts 13 =.500 c. "" VnIlto System S...E ".

Hodup co pesr odu 8 a3 Inekg EA filter a ainmenttaio Contde yse 1000 Filteroo 5 1f 000 7,ooler 2000 cfmr T VSRoughingHEAFle Ho ldpTanks Exhus filte HEP0 cfor reuse -U::f Laundry cfrý Area(:25 u Area 2 0 0 G ar afTn k (6 ec 1 1 ,2 0 Containuent Moi ortingnsr mentato ga Waste New Ra ,cHEP Holdupn co p esr a ePrec f l er Filter A

Tanks~~ 1350fm ~ 50 000 f OutsidAirS 1350 C h e ntic latindVl eCotlSystem 14-

SA - tem Je irEeco FulPt -] 0 Eflun 0 0 Moiorn ntriet tio Ar. reiler cfAra3reile 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS FIGURE 3-2 LOCATIONS OF AIRBORNE EFFLUENT DOSE CALCULATIONS Locations at which doses due to airborne effluent the Turkey Point Nuclear Plant are calculated:

1. Beta and gamma doses to air, 1950 meters SSE.

2. Maximally exposed person, 5800 meters WNW.

3. Assumed beef and milk cow, 7250 meters W.

II CANAL I 5fl-CANAL FALM DRIVE TURKEY POINT PLANTw 3-9 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENT CONTROL 3.11: Radioactive Gaseous Effluent Monitoring Instrumentation; Operability and Alarm/Trip Setpoints The radioactive gaseous effluent monitoring instrumentation channels shown in Table 3.1-1 shall be OPERABLE with their Alarm/Trip Setpoints set to ensure that the limits of Control 3.2 are not exceeded. The Alarm/Trip Setpoints of these channels meeting Control 3.2 shall be determined and adjusted in accordance with the methodology and parameters in this ODCM.

APPLICABILITY: As shown in Table 3.1-1 ACTION:

a. With a radioactive gaseous effluent monitoring instrumentation channel Alarm/Trip Setpoint less conservative than required by the above specification, immediately suspend the release of radioactive gaseous effluents monitored by the affected channel, or declare the channel inoperable or change the set point so it is acceptably conservative.

b. With less than the minimum number of radioactive gaseous effluent monitoring instrumentation channels OPERABLE, take the ACTION shown in Table 3.1-1.

Restore the inoperable instrumentation to OPERABLE status within 30 days and, if unsuccessful explain in the next Annual Radioactive Effluent Release Report pursuant to Administrative Control 1.3 why this in operability was not corrected in a timely manner.

c. The provisions of Administrative Control section 1.6.3 are not applicable.

SURVEILLANCE REQUIREMENTS Each radioactive gaseous effluent monitoring instrumentation channel shall be demonstrated OPERABLE by performance of the CHANNEL CHECK, SOURCE CHECK, CHANNEL CALIBRATION and ANALOG CHANNEL OPERATIONAL TEST at the frequencies shown in Table 3.1-2.

3-10 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENT CONTROL 3.11: Radioactive Gaseous Effluent Monitoring Instrumentation, Operability and Alarm/Trip Setpoints, (continued)

TABLE 3.1-1 RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION MINIMUM CHANNELS INSTRUMENT 0 'PERABLE APPLICABILITY ACTION

1. GAS DECAY TANK SYSTEM

a. Noble Gas Activity Monitor -

Providing Alarm and Automatic Termination of Release 1

3.1.1 (Plant Vent Monitor)

b. Effluent System Flow Rate Measuring Device 1 3.1.2

2. Condenser Air Ejector Vent System

a. Noble Gas Activity Monitor (SPING or PRMS) 1 3.1.3

b. Iodine Sampler 1 3.1.6

c. Particulate Sampler 1 3.1.6

d. Effluent System Flow Rate Measuring Device 1 3.1.2

e. Sampler Flow Rate Measuring Device 1 3.1.5 3-11 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENT CONTROL 3.1* Radioactive Gaseous Effluent Monitoringq Instrumentation: Operability and Alarm/Trip Setpoints, (continued)

TABLE 3.1-1 (continued)

RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION MINIMUM CHANNELS INSTRUMENT 0OPERABLE APPLICABILITY ACTION

3. Plant Vent System (Include Unit 4's Spent Fuel Pool)

a. Noble Gas Activity Monitor (SPING or PRMS) 1

3.1.3

b. Iodine Sampler 1

3.1.4

c. Particulate Sampler 1

3.1.4

d. Effluent System Flow Rate Measuring Device 1 3.1.2

e. Sampler Flow Rate Measuring Device 1 3.1.5

4. Unit 3 Spent Fuel Pit Building Vent

a. Noble Gas Activity Monitor 1 3.1.3

b. Iodine Sampler 1 3.1.4

c. Particulate Sampler 1

3.1.4

d. Sampler Flow Rate Measuring Device 1

3.1.5 3-12 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENT CONTROL3.1: Radioactive Gaseous Effluent Monitoring Instrumentation: Operability and Alarm/Trip Setpoints, (continued)

TABLE 3.1-1 (Continued)

TABLE NOTATION

r At all times.

Applies during MODE 1, 2, 3 and 4.

Applies during MODE 1, 2, 3 and 4 when primary to secondary leakage is detected.

ACTION 3.1.1 - With the number of channels OPERABLE less than required by the Minimum Channels OPERABLE requirement, the contents of the tank(s) may be released to the environment provided that prior to initiating the release:

a. At least two independent samples of the tank's contents are analyzed, and

b. At least two technically qualified members of the facility staff independently verify the release rate calculations and discharge valve lineup; Otherwise, suspend release of radioactive effluents via this pathway.

ACTION 3.1.2 - With the number of channels OPERABLE less than required by the Minimum Channels OPERABLE requirement, 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 .

ACTION 3.1.3 - With the number of channels OPERABLE-less than required by the Minimum Channels OPERABLE requirement, effluent releases via this pathway may continue provided grab samples are taken at least once per 12 hours1.388889e-4 days 0.00333 hours 1.984127e-5 weeks 4.566e-6 months and these samples are analyzed for radioactivity within 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months .

SAMPLING EVOLUTIONS are not an interruption of the continuous sample collection requirement and do not render the channel INOPERABLE. If a SAMPLE EVOLUTION is unable to be completed, THEN perform the actions for an INOPERABLE channel within 4 hours4.62963e-5 days 0.00111 hours 6.613757e-6 weeks 1.522e-6 months of the start of the SAMPLING EVOLUTION.

ACTION 3.1.4 With the number of channels OPERABLE less than required by the Minimum Channels OPERABLE requirement, effluent releases via the affected pathway may continue provided continuous sample collection with auxiliary equipment as required by Table 3.2-1 is installed within 4 hours4.62963e-5 days 0.00111 hours 6.613757e-6 weeks 1.522e-6 months of the channel being declared INOPERABLE, and analyzed at least weekly.

3-13 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENT SAMPLING EVOLUTIONS are not an interruption of the continuous sample collection requirement and do not render the channel INOPERABLE. If a SAMPLING EVOLUTION is unable to be completed, THEN perform the actions for an INOPERABLE channel within 4 hours4.62963e-5 days 0.00111 hours 6.613757e-6 weeks 1.522e-6 months of the start of the SAMPLING EVOLUTION.

ACTION 3.1.5 With the number of channels OPERABLE less than required by the Minimum Channels OPERABLE requirement, effluent releases via the affected pathway may continue provided auxiliary equipment is installed, AND the sample flow rate is verified at least once per 4 hours4.62963e-5 days 0.00111 hours 6.613757e-6 weeks 1.522e-6 months .

ACTION 3.1.6 Continuous collection of iodine and particulate in the Condenser Air Ejector is not required. If Primary to Secondary leakage is detected, effluent releases via the affected pathway may continue provided that the iodine and particulate curies released are determined using the methodology of Reference 3.

SAMPLING EVOLUTIONS are not an interruption of the continuous sample collection requirement and do not render the channel INOPERABLE. If a SAMPLING EVOLUTION is unable to be completed, THEN perform the actions for an INOPERABLE channel within 4 hours4.62963e-5 days 0.00111 hours 6.613757e-6 weeks 1.522e-6 months of the start of the SAMPLING EVOLUTION.

3-14 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENT CONTROL 3.11: Radioactive Gaseous Effluent Monitoring Instrumentation: Operability and Alarm/Trip Setpoints, (continued)

TABLE 3.1-2 RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION SURVEILLANCE REQUIREMENTS ANALOG CHANNEL MODES FOR WHICH CHANNEL SOURCE CHANNEL OPERATIONAL SURVEILLANCE IS INSTRUMENT CHECK CHECK CALIBRATION TEST REQUIRED

1. GAS DECAY TANK SYSTEM

a. Noble Gas Activity Monitor Providing Alarm and Automatic Termination of Release P P R (3) Q(1)

(Plant Vent Monitor)

b. Effluent System Flow Rate Measuring Device P (4) N.A. R N.A.

2. Condenser Air Ejector Vent System

a. Noble Gas Activity Monitor (SPING or PRMS) D M R (3) Q (2)

b. Effluent System Flow Rate Measuring Device D (4) N.A. R N.A. ##I

c. Sample Flow Rate Measuring Device D (4) N.A. R N.A.

3-15 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENT CONTROL 3.11: Radioactive Gaseous Effluent Monitoring Instrumentations Operability and Alarm/Trip Setpoints, (continued) I TABLE 3.1-2 (Continued)

RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION SURVEILLANCE REQUIREMENTS ANALOG CHANNEL MODES FOR WHICH CHANNEL SOURCE CHANNEL OPERATIONAL SURVEILLANCE IS INSTRUMENT CHECK CHECK CALIBRATION TEST REQUIRED

3. Plant Vent System (Include Unit 4's Spent Fuel Pool)

a. Noble Gas Activity Monitor (SPING or PRMS) D M R (3) Q (2)

b. Iodine Sampler W (5) N.A. N.A. N.A.

c. Particulate Sampler W (5) N.A. N.A. N.A. *

d. Effluent System Flow Rate Measuring Device D (4) N.A. R N.A.

e. Sampler Flow Rate Measuring Device D (4) N.A. R N.A.

4. Unit 3 Spent Fuel Pit Building Vent

a. Noble Gas Activity Monitor D M R (3) Q (2)

b. Iodine Sampler W (5) N.A. N.A. N.A.

C. Particulate Sampler W (5) N.A. N.A. N.A. *

d. Sampler Flow Rate Measuring Device D (4) N.A. R N.A.

3-16 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENT CONTROL 3.1* Radioactive Gaseous Effluent Monitoring Instrumentation: Operability and Alarm/Trip Setpoints, (continued)

TABLE 3.1-2 (Continued)

TABLE NOTATIONS

At all times during periods of release.

Applies during MODE 1, 2, 3 and 4.

1. Applies during MODE 1, 2, 3 and 4 when primary to secondary leakage is detected.

(1) The ANALOG CHANNEL OPERATIONAL TEST shall also demonstrate that automatic isolation of this pathway and control room alarm annunciation occurs if the instrument indicates measured levels above the Alarm/Trip Setpoint.

(2) The ANALOG CHANNEL OPERATIONAL TEST shall also demonstrate that if the instrument indicates measured levels above the Alarm Setpoint, alarm annunciation occurs in the control room (for PRMS only) and in the computer room (for SPING only).

(3) The initial CHANNEL CALIBRATION shall be performed using one or more of the reference standards certified by the National Institute of Standards and Technology (NIST) or using standards that have been obtained from suppliers that participate in measurement assurance activities with NIST. When practical, these standards shall permit calibrating the system over its intended range of energy and measurement range.

For subsequent CHANNEL CALIBRATION, sources that have been related to the initial calibration shall be used.

(4) 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 CHECK shall consist of changing and analyzing the filter on a weekly basis.

3-17 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENT CONTROL 3.1" Radioactive Gaseous Effluent Monitoring Instrumentation: Operability and Alarm/Trip Setpoints, (continued)

METHOD 3.1.1: GASEOUS EFFLUENT MONITOR SURVEILLANCES The surveillances of Gross Radioactivity Monitors Providing Alarm and Automatic Termination of Release and Flow Rate Measurement Devices are scheduled by procedure 0-ADM-215, Plant Surveillance Tracking Program.

METHOD 3.1.2: ESTABLISHING GASEOUS EFFLUENT MONITOR ALARM AND TRIP SETPOINTS The radioactive gaseous effluent monitoring instrumentation channels alarm setpoints and trip setpoints are set in accordance with Control 3.1 to ensure the limits of Control 3.2 are not exceeded.

Each radioactive noble gas effluent monitor setpoint is derived on the basis of total body dose equivalent rate at or beyond the site boundary.

For the purpose of deriving a setpoint, the distribution of radioactive noble gases in an effluent stream may be determined in one of the following ways:

o Preferably, the radionuclide distribution is obtained by gamma spectrum analysis of identifiable noble gases in effluent gas samples. Results of analysis of one or more samples may be averaged to obtain a representative spectrum.

o Altemately, the total activity concentration of radioactive noble gases may be assumed to be Xe-133. This approach is valid because Xe-133 contributes about 99% of the noble gas activity.

3-18 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENT CONTROL 3.1 : Radioactive Gaseous Effluent Monitorinq Instrumentation: Operability and Alarm/Trip Setpoints, (continued)

METHOD 3.1.2: ESTABLISHING GASEOUS EFFLUENT MONITOR ALARM AND TRIP.

SETPOINTS (continued)

A noble gas effluent monitor alarm and trip setpoint, based on dose rate, is calculated with the equation below, or a method which gives a lower setpoint value in accordance with approved plant procedures.

S= 1.06 h /Q L _(Ci + Bkg Eqn 3.1-1 where:

S = The alarm setpoint, (cpm) 1.06 = conversion constant (500 mrem/yr.60 sec/min 35.32 ft3/m 3 - 1 m3/10 6cm 3) h = monitor response to activity concentration of effluent, crn (JACi/cc)

F = flow of gaseous effluent stream, i.e., flow past the monitor, (ft3/min)

X/Q = atmospheric dispersion factor at the off-site location of interest, (sec/n3)

Ci= concentration of radionuclide i in gaseous effluent (pCi/cc).

DF = Dose factor for exposure to a semi-infinite cloud of noble gas, mrem See Table 3.1-3. (yr-pCi/m 3)

Sf= A factor to allow for multiple sources from different or common release points. The allowable operating setpoints will be controlled administratively by assigning a fraction of the total allowable release to each of the release sources. For gas releases, this fraction is assigned as follows: 0.6 for the Plant Vent, 0.1 for the 3 Spent Fuel Pit Vent, 0.1 for each SJAE Vent, and 0.1 for unmonitored gas releases.

Bk = Instrument background count rate, cpm 3-19 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENT CONTROL 3.11: Radioactive Gaseous Effluent Monitoring Instrumentation: Operability and Alarm/Trip Setpoints, (continued)

METHOD 3.1.2: ESTABLISHING GASEOUS EFFLUENT MONITOR ALARM AND TRIP SETPOINTS, (continued)

Each monitoring channel has a unique response, h, which is determined by the instrument calibration.

Atmospheric dispersion depends upon the local atmospheric conditions. For the purpose of calculating a radioactive noble gas effluent monitor setpoint, the atmospheric dispersion factor, X/Q, will be based on prevailing meteorological conditions or on reference meteorological conditions. The minimum atmospheric dispersion off site 3 derived from reference meteorological conditions at the site boundary is 5.8 x 10- sec/m at a location 1950 meters south southeast of the plant.

The applicable dose conversion factors, DFj, for deriving setpoints are in Table 3.1-3.

The limiting factor for equation 3.1-1 is the total body dose rate limit of 500 mrem/year which is included in the 1.06 conversion factor. The use of the total body dose assumes that the total body dose will be the controlling dose rate and the dominant contributor to this dose will be Xe-1 33.

Each iodine and particulate effluent monitor setpoint may be calculated using equation 3.1-2, or a method which gives a lower setpoint value. Since the iodine and particulate channels are not required by Control 3.1, the primary method to ensure Control 3.2 is met is the performance of the sampling and analysis program in table 3.2-1 and the noble gas alarm setpoints.

3 - 20 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENT CONTROL 3.1 : Radioactive Gaseous Effluent Monitoring Instrumentation: Operability and Alarm/Trip Setpoints, (continued)

METHOD 3.1.2: ESTABLISHING GASEOUS EFFLUENT MONITOR-ALARM AND TRIP SETPOINTS (continued)

S

=s DR 9 h 9 Sf 9 3600tvR S

t *VR+ BKG+ KEq3.- Eqn 3.1-2 TAanp

. lxQ where:

DR = the dose rate limit the effluent pathway is limited to; 1500 mrem/year.

Taanip = a factor relating the airborne concentration time integral of radionuclide i to the dose equivalent to organ, n, of a person in age group, a, exposed via pathway, p (inhalation), as described in Method 3.2, See Appendix 3B. mrem/vr (pCi/m 3 )

3600 = conversion constant, (sec/hr).

h = monitor response to activity deposited on the sample collection media, cpm/uCi.

t = period of time over which the effluent release takes place, (hours).

Xd/Q = atmospheric dispersion factor adjusted for depletion by deposition at the off-site location of interest (sec/rn3).

Sf= A factor to allow for multiple sources from different or common release points. The allowable operating setpoints will be controlled administratively by assigning a fraction of the total allowable release to each of the release sources. For gas releases, this fraction is assigned as follows: 0.6 for the Plant Vent, 0.1 for the 3 Spent Fuel Pit Vent, 0.1 for each SJAE Vent, and 0.1 for unmonitored gas releases.

VR = Ratio of sample volume to release volume.

3-21 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENT CONTROL 3.1 : Radioactive Gaseous Effluent Monitoring Instrumentation: Operability and Alarm/Trip Setpoints, (continued)

METHOD 3.1.2: ESTABLISHING GASEOUS EFFLUENT MONITOR ALARM AND TRIP SETPOINTS, (continued)

BASIS 3.11:

The radioactive gaseous effluent 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 to ensure that the alarm/trip will occur prior to exceeding the limits of 10 CFR Part 20. The noble gas effluent monitors Alarm/Trip setpoint is calculated using equation 3.1-1. It is shown in example calculation 3.1.2, that for continuous releases, the calculated setpoint exceeds the range of the monitor. Lower setpoints are therefore set in accordance with approved plant procedures. Typically, the Alarm setpoint for continuous releases, is set at a small fraction of the instrument's range to alert operators of an adverse trend. During continuous releases there is no process to trip; therefore, a trip setpoint is not determined for a continuous release. The sensitivity of any noble gas activity monitors used to show compliance with the gaseous effluent release requirements of Control 3.3 shall be such that concentrations as low as 1 x 10- jCi/ml are measurable.

This instrumentation also includes provisions for monitoring (and controlling) the concentrations of potentially explosive gas mixtures in the GAS DECAY TANK SYSTEM.

The OPERABILITY 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 - 22 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENT CONTROL 3.1

Radioactive Gaseous Effluent Monitoring Instrumentation: Operability and Alarm/Trip Setpoints, (continued)

- METHOD 3.1.2: ESTABLISHING GASEOUS EFFLUENT MONITOR ALARM AND TRIP SETPOINTS, (continued)

TABLE 3.1-3 DOSE FACTORS, DF, FOR EXPOSURE TO A SEMI-INFINITE CLOUD OFNOBLE GAS mrem 3 yr PCi/ m Radionuclide Kr-83m 7.56 E-2 Kr-85m 1.17 E3 Kr-85 1.61 El Kr-87 5.92 E3 Kr-88 1.47 E4 Kr-89 1.66 E4 Kr-90 1.56 E4 Xe-131m 9.15 El Xe-1 33m 2.51 E2 Xe-i 33 2.94 E2 Xe-1 35m 3.12 E3 Xe-1 35 1.81 E3 Xe-1 37 1.42 E3 Xe-1 38 8.83 E3 Xe-1 39 5.02 E3 Ar-41 8.84 E3 Source: RG1.109 table B-i, values multiplied by 1.0 x 106 to convert pCi to uCi.

3 - 23 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENT CONTROL 3.1: Radioactive Gaseous Effluent Monitoring Instrumentation: Operability and Alarm/Trip Setpoints, (continued)

METHOD 3.1.2: ESTABLISHING GASEOUS EFFLUENT MONITOR-ALARM AND TRIP SETPOINTS, (continued)

EXAMPLE CALCULATION: Determining the Noble Gas Monitor Alarm Setpoint Control 3.1 requires release setpoints to be based on a dose rate. Derivations used to determine setpoints assume that noble gas releases occur at ground level. The noble gas effluent monitor setpoint, based on dose rate is calculated using Equation 3.1-1.

I Ci S = 1.06 -h Sf . + Bkg F I/Q YZ(Ci

DFi) where:

S = The alarm setpoint (CPM).

3 3 1.06 = Conversion factor; 500 mrem *60 sec- 35.32 ft - 1m yr min m 3 106 cc h = Monitor response to activity concentration of effluent com (pCi/cc).

F = Flow of gaseous effluent stream past the monitor ft3 (min).

x/Q = atmospheric dispersion factor at the offsite location of interest, sec (me)

Sf = a factor to allow for multiple sources from different or common release points. The allowable operating setpoints will be controlled by assigning a fraction of the allowable release to each of the release sources. For gas releases, this fraction is assigned as follows: 0.6 for the Plant Vent, 0.1 for the 3 Spent Fuel Pit Vent, 0.1 for each SJAE Vent, and 0.1 for unmonitored gas releases.

3 - 24 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENT CONTROL 3.11" Radioactive Gaseous Effluent Monitoring Instrumentation: Operability and Alarm/Trip Setpoints, (continued)

METHOD 3.1.2: ESTABLISHING GASEOUS EFFLUENT MONITOR ALARM AND TRIP SETPOINTS, (continued)

EXAMPLE CALCULATION: Determining the Noble Gas Monitor Alarm Setpoint, (continued)

DFi = factor for exposure to a semi-infinite cloud of noble gas mrem see Table 3.1-3. (yr-p.Ci/m 3)

Ci = concentration of radionuclide, i, in gaseous effluent (p.Ci/cc).

Bkg = monitoring instrument background (cpm).

Example:

The measured concentration of noble gases to be discharged to the atmosphere are:

Radionuclide C CCi/c)

Kr-85m 3.6 x 10-W Kr-85 2 .8 x 104 Kr-87 2.5 x 106 Kr-88 1.4 x 10-Xe-131m 1.0 x 10-2 Xe-133 4.3 x 10-2 Xe-135 6.0 x 104 Ar-41 7.7 x 10-5 Determine the alarm setpoint, S (cpm) when:

h = 2.5x 108 cpm pCi/cc F = 8.0 x 104 ft3 min X/Q = 5.8 x 10-7 sec 3

mi Sf = 0.6 Bkg = 600 cpm CONTROL 3.1 : Radioactive Gaseous Effluent Monitoring Instrumentation: Operability and Alarm/Trip Setpoints, (continued)

METHOD 3.1.2: ESTABLISHING GASEOUS EFFLUENT MONITOR ALARM AND TRIP SETPOINTS, (continued) 3 - 25 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENT EXAMPLE CALCULATION: Determining the Noble Gas Monitor Alarm Setpoint, (continued)

Calculate the effect of a ground level release as follows:

Radionuclide Ci DFi Ci x DFi Kr-85m 3.6 x 10-5 1.17 x 103 4.2 x 10-2 Kr-85 2.8 x 10-4 1.61 x 10 1 4.5 x 10-3 Kr-87 2.5 x 10-6 5.92 x 10 3 1.5 x 10-2 Kr-88 1.4 x 10-5 1.47 x 104 2.1 x 10-1 Xe-131m 1.0x 10-2 9.15x 10 1 9.1 x 10-1 Xe-133 4.3 x 10-2 2.94 x 102 1.3 x 10 1 Xe-135 6 .0 x 104 1.81 X 103 1.1 x 100 Ar-41 7.7 x 10. 5 8.85 x 103 6.8 x 10-1 XCi =5.4 x 10-2 XCiDF =1.6 x 10 1 Calculate the setpoint as follows:

S =1.06 r2.5x 108 0 0.6 5 .4 x 10 2 ' +600 6

L 8.Ox104 " 5.8x 10-7 1. x 10'

= 1.06 [3.23x 109 ][3.4x 10-3] +600

= 11,565,794 cpm Note: The range of the installed monitor is 300,000 cpm, therefore, the alarm setpoint is set in accordance with plant procedures.

3 - 26.

11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.2: DOSE RATE FROM RADIOACTIVE GASEOUS EFFLUENTS The- dose rate due to radioactive materials released in gaseous effluents from the site to areas at and beyond the SITE BOUNDARY (see Figure 1.5-1) shall be limited to the following:

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

b. For Iodine-1 31, for Iodine-1 33, for tritium, and for all radionuclides in particulate form with half-lives greater than 8 days: Less than or equal to 1500 mrem/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 3.2.1 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 this ODCM.

3.2.2 The dose rate due to Iodine 131, Iodine 133, tritium, and all 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 this ODCM by obtaining representative samples and performing analyses in accordance with the sampling and analysis program specified in Table 3.2-1.

3 - 27 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.2: DOSE RATE FROM RADIOACTIVE GASEOUS EFFLUENTS. (continued)

TABLE 3.2-1 RADIOACTIVE GASEOUS WASTE SAMPLING AND ANALYSIS PROGRAM GASEOUS SAMPLING MINIMUM ANALYSIS TYPE OF LOWER LIMIT OF DETECTION RELEASE TYPE FREQUENCY FREQUENCY ACTIVITY ANALYSIS (LLD)"1), (1pCi/cc)

1. Gas Decay Tank P P Principal Gamma Emitters (2) 1 x 10-4 (Batch) Each Tank, Grab Sample Each Tank

2. Containment Purge or P (6) p (6) Principal Gamma Emitters (2) 1 x 10.4 Venting (Batch)

Grab Sample Each PURGE H-3 1 x 10-6

3. Condenser Air Ejectors M (6) M(6) Principal Gamma Emitters (2) 1 x 10-4 Grab Sample Gas Sample H-3 1x 10-

4. Plant Vent (includes Unit 4 M (6) M(6) Principal Gamma Emitters (2) 1 x 10-4 Spent Fuel Pit Building Grab Sample Gas Sample Vent)

M (4),(5) M H-3 1 x 106 Grab Sample

5. Unit 3 Spent Fuel Pit M M Principal Gamma Emitters (2) 1 x 104 Building Vent Grab Sample Gas Sample M M H-3 1 X10-6 Grab Sample

6. All Release Types as listed Continuous (3)(9) W (7)(8) 1-131 1 x 10.12 in 3,4, and 5 (above) Charcoal Sample Continuous (3)(9) W (7)(8) Principal Gamma Emitters (2) 1 x 10.11 Particulate Sample Continuous (3)(9) M (8) Gross Alpha Composite Particulate sample 1 x 10-1 Continuous (3)(9) Q (6) Sr-89, Sr-90 Composite Particulate sample l x 10.11 Continuous (3)(9) Noble Gas Monitor Noble Gas Gross Beta or Gamma I x 10"6 3 - 28 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS -

CONTROL 3.2: DOSE RATE FROM RADIOACTIVE GASEOUS EFFLUENTS, (continued)

TABLE 3.2-1, (Continued)

TABLE NOTATIONS (1) The LLD is the smallest concentration of radioactive material in a sample 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 radio chemical separation:

LLD = 4.66S__b E x V x (2.22 x 106) x Y x [exp (-kAt)]

Where:

LLD = The "a priori" lower limit of detection as defined above as a blank sample (microCurie per unit mass or volume),

s = The counting rate of a blank sample or the standard deviation of the background counting rate as appropriate (counts per minute),

E = The counting efficiency (counts per disintegration)

V = The sample size (units of mass or volume),

2.22 x 106 = The number of disintegrations per minute per microCurie, Y = The fractional radio chemical yield, when applicable, S= The radioactive decay constant for the particular radionuclide, and At = The elapsed time between the midpoint of sample collection and the time of counting (for plant effluents, not environmental samples)

Typical values of E, V, Y and At shall be used in the calculation.

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.

3 - 29 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.2: DOSE RATE FROM RADIOACTIVE GASEOUS EFFLUENTS, (continued)

TABLE 3.2-1 (Continued)

TABLE NOTATIONS (Continued)

(2) The principal gamma emitters for which the LLD specification will apply are exclusively the following radionuclides: Kr-87, Kr-88, Xe-1 33, Xe-133m, Xe-1 35, and Xe-1 38 in noble gas emissions and Mn-54, Fe-59, Co-58, Co-60, Zn-65, Mo-99, 1-131, Cs-134, Cs-137, Ce-141 and Ce-144 for particulate emissions. This list does not mean that only these nuclides are to be detected and reported. Other gamma peaks that are measurable and identifiable, together with the above nuclides, shall also be identified and reported pursuant to Administrative Control 1.3.

Nuclides which are below the LLD for the analyses should not be reported as being present at the LLD for that nuclide. When a radionuclide's calculated LLD is greater than its listed LLD limit, the calculated LLD should be assigned as the activity of the radionuclide; or, the activity of the radionuclide should be calculated using measured ratios with those radionuclides which are routinely identified and measured.

(3) The 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 3.2, 3.3, and 3.4.

(4) When a Unit's refueling canal is flooded, Tritium grab samples shall be taken on that Unit only from the following respective area(s) at least once per 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months :

For Unit 3 sample the plant vent and the Unit 3 spent fuel pool area ventilation exhaust.

For Unit 4 sample the plant vent only.

(5) When spent fuel is in the spent fuel pool, tritium grab samples shall be taken from the following respective area at least once per 7 days:

For Unit 3, sample the Unit 3 spent fuel pool area ventilation exhaust For Unit 4, sample the plant vent.

3 - 30 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.2: DOSE RATE FROM RADIOACTIVE GASEOUS EFFLUENTS. (continued)

TABLE 3.2-1 (Continued)

TABLE NOTATIONS (Continued)

(6) Sampling and analysis shall also be performed following shutdown, startup, or a THERMAL POWER change exceeding 15% of RATED THERMAL POWER within a 1 hour1.157407e-5 days 2.777778e-4 hours 1.653439e-6 weeks 3.805e-7 months period if (1)analysis shows that the DOSE EQUIVALENT 1-131 concentration in the primary coolant has increased by more than a factor of 3; and (2)the noble gas activity monitor shows that effluent activity has increased by more than a factor of 3.

(7) Sample collection media on the applicable Unit 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. Sample collection media on the applicable Unit shall also be changed at least once per 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months for at least 7 days following each shutdown, startup, or THERMAL POWER change exceeding 15% of RATED THERMAL POWER within a 1 hour1.157407e-5 days 2.777778e-4 hours 1.653439e-6 weeks 3.805e-7 months period and analyses shall be completed within 48 hours5.555556e-4 days 0.0133 hours 7.936508e-5 weeks 1.8264e-5 months of changing if: (1)analysis shows that the DOSE EQUIVALENT 1-131 concentration in the primary coolant has increased more than a factor of 3; and (2)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 LLD's may be increased by a factor of 10.

(8) The condenser Air Ejectors pathway is not isokinetic and therefore monitoring of iodine and particulate is not representative. The iodine and particulate curies released are determined using the methodology of Reference 3.

(9) SAMPLING EVOLUTIONS are not an interruption of the continuous sample collection requirement and do not render the channel INOPERABLE. Ifa SAMPLING EVOLUTION is unable to be completed, THEN perform the actions for an INOPERABLE channel within 4 hours4.62963e-5 days 0.00111 hours 6.613757e-6 weeks 1.522e-6 months of the start of the SAMPLING EVOLUTION.

3 -31 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS METHOD 3.2 Dose Rate Due to Gaseous Effluent Compliance with the limits on dose rate from noble gases is demonstrated by establishing effluent monitor alarm setpoints such that an alarm will occur at or before a dose rate limit of the combined releases for noble gasesis reached for the release types listed in ODCM Table 3.2-1. Ifan alarm occurs when the monitor setpoint is at or below the limit, compliance may be assessed by comparing the monitor record with the setpoint (limit) calculated in accordance with Method 3.1.2 or a more conservative method calculated in accordance with approved plant procedures. In the event an alarm occurs and the monitored release exceeds the setpoint limit, then compliance shall be evaluated by calculating dose rates in accordance with Methods A and B, below.

The alarm setpoints shall be derived on the basis of the radionuclide distribution from a measured gamma spectrum, or by assuming the total noble gas activity is Xe-133. IfXe-133 is the dominant radioactive gas in the airborne effluent, the gamma dose rate to a person's body is expected to be a larger fraction of the 500 mrem/year limit than is the sum of beta and gamma dose rates to the skin limit of 3000 mrem/year. Thus, a gaseous effluent monitor setpoint may be derived on the basis of whole body gamma dose rate alone such that an alarm occurs at or before the whole body dose rate off site exceeds 500 mrem/year as given in Control 3.2.

3 - 32 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.2: DOSE RATE FROM RADIOACTIVE GASEOUS EFFLUENTS, (continued)

METHOD 3.2: Dose Rate Due to Gaseous Effluent, (continued)

A. TOTAL BODY DOSE RATE The total body dose rate from radioactive noble gases may be calculated at any location off-site by assuming a person is immersed in and irradiated by a semi-infinite cloud of the noble gases. The dose rate is calculated using the equation X I DTB - - 1 p Eqn 3.2-1 Qt 1 where:

DTB = Dose rate to total body from noble gases,(mrem/year)

X/Q = atmospheric dispersion factor at the off-site location of interest, (sec/m 3) t = Averaging time of release, i.e., increment of time during which Qj was released, (year)

QI = quantity of noble gas radionuclide i released during the averaging time, (GCi)

Pyi = factor converting time integrated concentration of noble gas radionuclide, i, at ground level to total body dose, mrem - M3 ; see Table 3.2-2.

(pCi - sec)

Since dose rate limits for airborne effluents apply everywhere off-site, compliance is assessed and alarm setpoints determined at the site boundary where the minimum atmospheric dispersion from the plant (maximum X/Q) occurs. That location is selected on the basis of reference meteorology data in Appendix 3A-1. According to those data, the minimum dispersion off-site occurs at the site boundary 1950 meters SSE of the plant where X/Q = 5.8 x 10-7 sec/m3.

3 - 33 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.2: DOSE RATE FROM RADIOACTIVE GASEOUS EFFLUENTS, (continued)

METHOD 3.2: Dose Rate Due to Gaseous Effluent, (continued)

B. Skin Dose Rate The dose rate to skin from radioactive noble gases may be calculated at any location off-site by assuming a person is immersed in and irradiated by a semi-infinite cloud of the noble gases. The dose rate to skin is calculated using the equation:

Ds DS

=QZ t.-[Y-Q " S# + .I11Q . Ay] Eqn. 3.2-2 where:

s= dose rate to skin from radioactive noble gases, (mrem/year)

S = factor converting time integrated concentration of noble gas radionuclide i at ground level, to skin dose from beta radiation, mrem 3 , see Table 3.2-2

(.tCi-sec/m 1.11 = ratio of tissue dose equivalent to air dose in a radiation field, (mrem/mrad)

Ayi = factor for converting time integrated concentration of noble gas radionuclide, i, in a semi-infinite cloud, to air dose from its gamma radiation, mrad , listed in Table 3.2-3 (VLCi-sec/m 3)

Since dose rate limits for airborne effluents apply everywhere off-site, compliance is assessed and alarm setpoints determined at the site boundary where the minimum atmospheric dispersion from the plant (maximum X/Q) occurs. That location is selected on the basis of reference meteorology data in Appendix 3A-1. According to those data, the minimum dispersion off-site occurs at the site boundary 1950 meters SSE of the plant where x/Q = 5.8 x 10 -7sec/m 3.

3 - 34 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.2: DOSE RATE FROM RADIOACTIVE GASEOUS EFFLUENTS,. (continued)

METHOD 3.2: Dose Rate Due to Gaseous Effluent, (continued)

C. H-3, 1-131, 1-133 and PARTICULATE DOSE RATE The dose rate to any organ due to H-3, 1-131, 1-133 and radioactive material in particulate form with a half-life of more than 8 days is calculated with the equation:

"- Q k

TAZdp Eqn 3.2-3 Q ik a where:

Danp = dose equivalent rate to body organ, n, of a person in age group, a, exposed via pathway, p, to radionuclide, i, identified in analysis, k, of effluent air, (mrem/year) 3600 = conversion constant, (sec/hr) t = period of time over which the effluent releases are averaged, (hr)

Xd/Q = atmospheric dispersion fkctor, adjusted for depletion by deposition(sec/m3).(Alternately X/Q, unadjusted, may be used).

Qik = quantity of radionuclide, i, released during time increment, t, based on analysis, k (pCi).

TAanip = a factor relating the airborne concentration time integral of radionuclide, i, to the dose equivalent to organ, n, of a person in age group, a, exposed via pathway, p (air-grass-cow-milk), mrem/yr See Appendix 3B.

(gCi/m 3)

When the dose rate due to H-3, 1-131,1-133 and radionuclides in particulate form is calculated for the purpose of assessing compliance with Control 3.2, a hypothetical infant located where the minimum atmospheric dispersion from the plant occurs is assumed as the receptor.

3 - 35 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.2: DOSE RATE FROM RADIOACTIVE GASEOUS EFFLUENTS, (continued)

METHOD 3.2: Dose Rate Due to Gaseous Effluent, (continued)

C. H-3, 1-131,1-133 and PARTICULATE DOSE RATE, (continued)

For the radioiodines and particulates with half-lives greater than eight days, the effective dose transfer factor, TAanip, is based solely on the radioiodines (1-131, 1-133).

This approach was selected because the radioiodines contribute essentially all of the dose to the infant's thyroid via the inhalation and the grass-cow-milk pathway. The infant's thyroid via the grass-cow-milk pathway is the critical organ and controlling pathway respectively for the releases of radioiodines and particulates.

The dose rate calculation will be based on the location of minimum dispersion adjusted for deposition according to the reference meteorology data in Appendix 3A-

2. According to those data, the minimum dispersion offsite occurs at the site boundary 1950 meters SSE of the plant and the Xd/Q value is 5.0 x 107 sec/m 3. That location is identified in Figure 3-2. Altemately, averaged meteorological dispersion data coincident with the period of release may be used to evaluate the dose rate.

These radionuclide concentrations in airborne effluents, Qik, are measured according to the sample and analysis schedule in ODCM Table 3.2-1 BASIS 3.2:

This control applies to the release of radioactive materials in gaseous effluents from all units at the site. The specified gamma and beta dose rates, above background, provides the datum against which the gaseous effluent monitor setpoints are determined, using the methods described in this ODCM, pursuant to Control 3.1. In essence, Control 3.2 is an instantaneous limit.

Adherence to Controls 3.3 through 3.5 provide assurance that levels of radioactive materials in air in UNRESTRICTED AREAS will, on the average, be a small fraction of the concentration limits and result in exposures to MEMBERS OF THE PUBLIC within the objectives of Appendix I to 10 CFR Part 50 and 40 CFR 190.

Control 3.2 permits the flexibility of operation, compatible with considerations of health and safety, to provide a dependable source of power even under circumstances that temporarily result in elevated releases, but still within the limit as specified in 10 CFR Part 20.1302 (b)(2)(ii).

3 - 36 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 - RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.2: DOSE RATE FROM RADIOACTIVE GASEOUS EFFLUENTS, (continued)

METHOD 3.2 : Dose Rate Due to Gaseous Effluent, (continued)

Table 3.2-2 Transfer Factors for Maximum Dose to a Person Offsite due to Radioactive Noble Gases Air Dose Transfer Factors Pý Sf3i mrem mrem Radionuclide (W.Ci sec/m 3) (4.Ci sec/m 3 )

Kr-83m 2.4E-9 --

Kr-85m 3.7E-5 4.6E-5 Kr-85 5.1 E-7 4.2E-5 Kr-87 1.9E-4 3.1 E-4 Kr-88 4.7E-4 7.5E-5 Kr-89 5.3E-4 3.2E-4 Kr-90 4.9E-4 2.3E-4 Xe-131m 2.9E-6 1.5E-5 Xe-133m 8.OE-6 3.1E-5 Xe-1 33 9.3E-6 9.7E-6 Xe-1 35m 9.9E-5 2.3E-5 Xe-1 35 5.7E-5 5.9E-5 Xe-1 37 4.5E-5 3.9E-4 Xe-138 2.8E-4 1.3E-4 Ar-41 2.8E-4 8.5E-5 Ref: Regulatory Guide 1.109, Revision 1, Table B-1.

Note: Values in the regulatory guide are quoted in units of pCi*yr, to convert to units of i*Ci*sec multiply by a factor of 3.171 E-2.

3 - 37 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.2: DOSE RATE FROM RADIOACTIVE GASEOUS EFFLUENTS, (continued)

METHOD 3.2: Dose Rate Due to Gaseous Effluent, (continued)

Table 3.2-3 Transfer Factors for Maximum Offsite Air Dose Air Dose Transfer Factors Ayi Api mrad mrad Radionuclide (.tCi sec/m 3 ) (iiCi sec/m 3 )

Kr-83m 6.1 E-7 9.1 E-6 Kr-85m 3.9E-5 6.2E-5 Kr-85 5.4E-7 6.2E-5 Kr-87 2.OE-4 3.3E-4 Kr-88 4.8E-4 9.3E-5 Kr-89 5.5E-4 3.4E-4 Kr-90 5.2E-4 2.5E-4 Xe-131m 4.9E-6 3.5E-5 Xe-133m 1.OE-5 4.7E-5 Xe-133 1.1E-5 3.3E-5 Xe-135m 1.1E-4 2.3E-5 Xe-135 6.1E-5 7.8E-5 Xe-1 37 4.8E-5 4.OE-4 Xe-138 2.9E-4 1.5E-4 Ar-41 2.9E-4 1.OE-4 Ref: Regulatory Guide 1.109, Revision 1, Table B-1 Note: Values in the regulatory guide are in units of pCi*yr, to convert to units of gCi*sec multiply by a factor of 3.171 E-2.

3 - 38 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.2: DOSE RATE FROM RADIOACTIVE GASEOUS EFFLUENTS, (continued)

METHOD 3.2 : Dose Rate Due to Gaseous Effluent, (continued)

EXAMPLE CALCULATIONS:. Dose Rate Due to Gaseous Effluent Determining the Total Body Dose Rate from Noble Gas The total body dose rate from the radioactive noble gases may be calculated at any location by assuming a person is immersed in and irradiated by a semi-infinite cloud of the noble gases. Compliance is assessed and alarm setpoints established based on the dose rate at the site boundary where the minimum atmospheric dispersion from the plant occurs. This location is 1950 meters SSE of the plant where X/Q = 5.8 x 10-7 sec/m 3 .

The dose rate D may be calculated using equation 3.2-1.

Example:

During a 31 day period, the following noble gas activity was released from Unit 3. The total body dose rate is calculated by:

DTB - Z , It Y Q1 0 Pri Q

where:

DTB = Dose rate to total body from noble gases, (mrem/year)

X/Q atmospheric dispersion factor at the off-site location of interest, (sec/m3) t = Averaging time of release, i.e., increment of time during which Qj was released, (year)

Q - quantity of noble gas radionuclide i released during the averaging time, (GtCi)

P7 i factor converting time integrated concentration of noble gas radionuclide, i, at ground level, to total body dose, mrem ; See Reference Table 3.2-2 (jtCi-sec/m3 )

3 - 39 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.2: DOSE RATE FROM RADIOACTIVE GASEOUS EFFLUENTS, (continued)

METHOD 3.2: Dose Rate Due to Gaseous Effluent, (continued)

EXAMPLE CALCULATIONS: Dose Rate Due to Gaseous Effluent, (continued)

The total body dose is summarized in the following table:

Radionuclide Qi Pyj QiPý Kr-85m 3.6E-2 3.7E-5 1.33E-6 Kr-85 2.8E-1 5.1 E-7 1.43E-7 Kr-87 2.5E-3 1.9E-4 4.75E-7 Kr-88 1.4E-2 4.7E-4 6.58E-6 Xe-131m 1.0E+1 2.9E-6 2.90E-5 Xe-1 33 4.3E+1 9.3E-6 4.OOE-4 Xe-1 35 6.OE-1 5.7E-5 3.42E-5 Ar-41 7.7E-2 2.6E-4 2.OOE-5 The value of YXQ iPyi is equal to 4.92 E-4 Note: The time (t) is for 31 day period stated as years which equals 31d/365d/yr or 0.085 yr.

The value of lit, in the equation, is 1/0.085 = 11.77.

D = 5.8 E-7 x 11.77 x 4.94 E-4 = 3.36 E-9 mRem/yr 3 -40 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.2 DOSE RATE FROM RADIOACTIVE GASEOUS EFFLUENTS, (continued)

METHOD 3.2: Dose Rate Due to Gaseous Effluent, (continued)

EXAMPLE CALCULATIONS: Dose Rate Due to Gaseous Effluent, (continued)

Determination of Skin Dose Rate from Noble Gases Example:

Using the noble gas release data given in the previous example, the skin dose rate is calculated by:

-S

Q - Sp; +I1Q ý Ds t 1 AT]

where:

S= dose rate to skin from radioactive noble gases (mrem/year)

Sp = factor converting time integrated concentration of noble gas radionuclide i at ground-level, to skin dose from beta radiation, mrem Reference Table 3.2-2 (jiCi-sec/m 3 )

1.11 = ratio of tissue dose equivalent to air dose in a radiation field, (mrem/mrad). -

A = factor for converting time integrated concentration of noble gas radionuclide i in a semi-infinite cloud, to air dose from its gamma radiation, mrad Listed in Table 3.2-3

(ýiCi.sec/m3) 3-41 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.2: DOSE RATE FROM RADIOACTIVE GASEOUS EFFLUENTS, (continued)

METHOD 3.2.: Dose Rate Due to Gaseous Effluent, (continued)

EXAMPLE CALCULATIONS : Dose Rate Due to Gaseous Effluent, (continued)

The skin dose rate is summarized in the following table:

Nuclide Qi Spi QiSii A,., QAo Kr-85m 3.6E-2 4.6E-5 1.7E-6 3.9E-5 1.40E-6 Kr-85 2.8E-1 4.2E-5 1.2E-5 5.4E-7 1.51 E-7 Kr-87 2.5E-3 3.1E-4 7.8E-7 2.OE-4 5.OOE-7 Kr-88 1.4E-2 7.5E-5 1.1E-6 4.8E-4 6.72E-6 Xe-131m 1.0E+1 1.5E-5 1.5E-4 4.9E-6 4.90E-5 Xe-133 4.3E-1 9.7E-6 4.2E-6 1.1 E-5 4.73E-6 Xe-135 6.OE-1 5.9E-5 3.5E-5 6.1E-5 3.66E-5 Ar-41 7.6E-2 8.5E-5 6.5E-6 2.9E-4 2.20E-5 The value of XQiSp = 2.11 E-4 and the value of YXQAy= 1.21 E-4 D =5.8E-7 x 11.77 (2.11E-4 + [1.11 x 1.21 E-4]) = 2.36 E-9 mrem/yr 3

Note: The value of lit is 11.77 (see previous Example table note), and X/Q is 5.8E-7 sec/m 3 - 42 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.2: DOSE RATE FROM RADIOACTIVE GASEOUS EFFLUENTS, (continued)

METHOD 3.2: Dose Rate Due to Gaseous Effluent, (continued)

EXAMPLE CALCULATIONS: Dose Rate Due to Gaseous Effluent, (continued)

Determining Dose Rate from Tritium, lodines, and Particulates The total body and/or organ dose rate due to tritium, radioiodines, and radioactive particulates with half-lives greater than 8 days released in the effluent air may be calculated at any location off-site using equation 3.2-3.

For assessing compliance with Control 3.2, the thyroid dose rate for a hypothetical infant located at the site boundary where the minimum atmospheric dispersion from the plant occurs is the assumed receptor.

Example:

During a calendar quarter (2184 hrs) the following activities were released from Unit 4. The dose rate from activity is calculated by:

=

1 _ d Y TAanip Danp 3600t Q k i where:

Danp = dose equivalent rate to body organ, n, of a person in age group, a, exposed via pathway, p, to radionuclide, i, identified in analysis, k, of effluent air, (mrem/year) 3600 = conversion constant, (sec/hr) t = period of time over which the effluent releases are averaged, (2184 hrs/qtr)

XdQ= quantity of radionuclide, i, released during time increment, t, based on analysis, k, (jiCi).

Qik = quantity of radionuclide, i, released during increment time, t, based on analysis, k, (gCi).

3 -43 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.2 : DOSE RATE FROM RADIOACTIVE GASEOUS EFFLUENTS, (continued)

METHOD 3.2: Dose Rate Due to Gaseous Effluent, (continued)

EXAMPLE CALCULATIONS: Dose Rate Due to Gaseous Effluent, (continued)

TAanip - a factor relating the airborne concentration time integral of radionuclide, i, to the dose equivalent to organ, n, of a person in age group, a (infant),

exposed via pathway, p (air-cow-grass-milk).

mrem/yr ; See Appendix 3B (jiCi/m 3 )

The dose rate from tritium; iodine and particulate is summarized in the following table.

Radionuclide Qik TAanip QikTAanip H-3 1.6E+5 2.37E+3 3.79E+8 Cr-51 8.OE-6 1.8E+4 1.44E-1 Co-58 5.OE-7 0 0 Co-60 9.5E-7 0 0 1-131 3.5E-7 9.94E-+11 3.48E+5 Cs-1 37 2.OE-6 0 0 Notes: The time factor 1/3600t = 1.27E-7 where t = 2184hrs/qtr The value of YQjkTAanip = 3.8E+8 The value of Xd/Q = 5.8E-7 Danp = 1.27E-7 x 5.8E-7 x 3.8E+8 = 2.8E-5 mrem/yr 3 -44 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS*

CONTROL 3.3: AIR DOSE FROM NOBLE GASES The air dose due to noble gases released in gaseous effluent, from each unit, to areas at and beyond the SITE BOUNDARY (see Figure 1.5 - 1) shall be limited to the following:

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

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

APPLICABILITY: At all times.

ACTION

a. 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 Control 1.6.6, 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.

b. The provisions of Administrative Control section 1.6.3 are not applicable.

SURVEILLANCE REQUIREMENTS 3.3.1 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 this ODCM at least once per 31 days.

3 -45 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.3: AIR DOSE FROM NOBLE GASES, (continued)

METHOD 3.3.1: NOBLE GAS GAMMA RADIATION DOSE The gamma radiation dose to air off site as a consequence of noble gas discharged from each unit can be calculated with the equation:

Dy = Q!EEQj..A,. Eqn 3.3-1 where:

Dy = noble gas gamma dose to air, (mrad)

Ayi = factor converting time integrated, ground level concentration of noble gas radionuclide i to air dose from gamma radiation listed in Table 3.3-1, mrad (pCi- sec/m 3)

X/Q = atmospheric dispersion factor at the off-site location of interest, (sec/m3)

Qj= the measured gaseous radioactivity released via a stack or vent during a single counting interval, j, (jiCi)

Surveillance 3.3.1 is satisfied by calculating the noble gas gamma radiation dose to air at the location identified in Figure 3-2. At that location, 1950 meters SSE of the Plant, the reference atmospheric dispersion factor to be used is x,/Q = 5.8 x 10-7 sec/m 3 .

Alternately, Surveillance 3.3.1 may be satisfied, when authorized for estimating doses due to an unplanned release, by calculating the gamma dose to air with the equation D,- x Arý, 0 Y Q, 0.8 Q Eqn 3.3-2 where:

0.8 = a conservative factor which, in effect, increases the estimated dose to compensate for variability in radionuclide distribution 3 -46 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.3: AIR DOSE FROM NOBLE GASES, (continued)

METHOD 3.3.1: Noble Gas Gamma Radiation Dose, (continued)

Ayef = effective gamma air dose factor converting time integrated, ground level, total activity concentration of radioactive noble gas, to air dose due to gamma radiation. This factor has been derived from noble gas radionuclide distributions in routine operational releases. (Refer to Appendix 3C for a detailed explanation). The effective gamma air dose factor is:

Ayeff 1.4 x 10-5 mrad (jtCi sec/m 3 )

The remaining factors have been defined previously.

METHOD 3.3.2: NOBLE GAS BETA RADIATION DOSE The beta radiation dose to air off site as a consequence of noble gas discharged from each unit can be calculated with the equation:

D,6 -IDZQj -AI Eqn 3.3-3 where:

D= noble gas beta dose to air, (mrad)

Ap=i factor converting time-integrated, ground level concentration of noble gas radionuclide i to air dose from beta radiation, listed in Table 3.3-1, mrad (pCi.-sec/m3)

=/Q atmospheric dispersion factor at the off-site location of interest, (sec/m3)

Surveillance 3.3.1 is satisfied by calculating the noble gas beta radiation dose to air at the location identified in Figure 3-2. At that location, 1950 meters SSE of the Plant, the reference atmospheric dispersion factor to be used is X/Q = 5.8 x 107 sec/m 3 .

3 -47 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.3: AIR DOSE FROM NOBLE GASES, (continued)

METHOD 3.3.2 Noble Gas Beta Radiation Dose, (continued)

Alternately, Control 3.3 may be satisfied, when authorized for estimating doses due to an unplanned release, by calculating the beta radiation dose to air with the equation 1 X oA Dp=0.8

-o08-Q Q * *YQj Eqn 3.3-4 where 0.8 = a conservative factor which, in effect, increases the estimated dose to compensate for variability in radionuclide distribution Aeff = effective beta air dose factor converting time integrated, ground level, total activity concentration of radioactive noble gas to air dose due to beta radiation. This factor has been derived from noble gas radionuclide distributions in routine operational releases. (Refer to Appendix 3C for a detailed explanation.) The effective beta air dose factor is:

Apeff =3.4 x 10-5 mrad (pCi sec/m 3)

The remaining factors have been defined previously.

3 - 48 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE. CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS -

CONTROL 3.3: AIR DOSE FROM NOBLE GASES. (continued)

BASIS 3.3:- DOSE - NOBLE GASES This Control applies to the release of radioactive materials in gaseous effluent from each unit at the site. For units with shared radwaste treatment systems, the gaseous effluents -

from the shared system are proportioned among the units sharing that system.

This control is provided to implement the requirements of Appendix 1,10 CFR Part 50. The Control implements the guides set forth in Appendix 1.The ACTION statements provide the required operating flexibility and at the same time implement the guides set forth in 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 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 under estimated. The dose calculation methodology and parameters established inthis ODCM for calculating the doses due to the actual release rates of radioactive noble gases in gaseous effluent 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.

3 -49 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.3: AIR DOSE FROM NOBLE GASES, (continued)

METHODS 3.3.1 & 3.3.2: Noble Gas Gamma & Beta Radiation Dose, (continued)

Table 3.3-1 Transfer Factors for Maximum Off site Air Dose Air Dose Transfer Factors Ayi mrad mrad 3

Radionuclide (u.Ci sec/mi ) (piCi sec/m 3)

Kr-83m 6.1 E-7 9.1 E-6 Kr-85m 3.9E-5 6.2E-5 Kr-85 5.4E-7 6.2E-5 Kr-87 2.OE-4 3.3E-4 Kr-88 4.8E-4 9.3E-5 Kr-89 5.5E-4 3.4E-4 Kr-90 5.2E-4 2.5E-4 Xe-1 31 m 4.9E-6 3.5E-5 Xe- 133m 1.OE-5 4.7E-5 Xe-1 33 1.1 E-5 3.3E-5 Xe-1 35m 1.1 E-4 2.3E-5 Xe-1 35 6.1E-5 7.8E-5 Xe-1 37 4.8E-5 4.OE-4 Xe-138 2.9E-4 1.5E-4 Ar-41 2.9E-4 1.OE-4 Ref. Regulatory Guide 1.109, Revision 1, Table B-1 Note Values in the regulatory guide are in units of pCi*yr, to convert to units of ptCi*sec multiply by a factor of 3.171 E-2.

3 - 50 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.3: AIR DOSE FROM NOBLE GASES, (continued)

EXAMPLE CALCULATION: AIR DOSE FROM NOBLE GASES Determining the Noble Gas Gamma Radiation Dose The cumulative dose due to gamma radiation from radioactive noble gases discharged from the plant shall be calculated once per 31 days to verify the quarterly and annual limits will not be exceeded.

The gamma radiation dose from noble gases are calculated at the site boundary where the minimum atmospheric dispersion occurs, i.e., 1950 meters SSE of the plant where X/Q = 5.8 x 10-7 sec/m3. The gamma dose is calculated using equation 3.3-1 or 3.3-2. The example given here uses equation 3.3-1.

Example:

The noble gas activity discharged during a 31 day period from gas decay tanks, containment purges, and the spent fuel pit vent were totaled as tabulated below. The gamma dose from the noble gas release is calculated as follows:

Dy - YZ Y Qj,, A4 (Eqn3.3-1)

Q j where:

Dy = The noble gas dose to air, (mrad).

x/Q = The atmospheric dispersion factor for a mixed-mode discharge, (sec/m 3 ).

Qj = The measured radioactivity released via stack or vent during a single counting interval, j (pCi).

A = Factor converting time integrated, ground-level concentration of noble gas radionuclide i to air dose from gamma radiation listed in Table 3.3-1 mrad (pCi.sec/mi3 )

3-51 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.3: AIR DOSE FROM NOBLE GASES, (continued)

EXAMPLE CALCULATION: AIR DOSE FROM NOBLE GASES, (continued)

The noble gas gamma radiation dose is summarized in the following table.

Radionuclide Qj Ayi QjAyi Kr-85m 5.4E+1 3.9E-5 2.1E-3 Kr-85 5.4E+1 5.4E-7 2.9E-5 Kr-87 5.4E+1 2.OE-4 1.1E-2 Kr-88 5.4E+1 4.8E-4 2.6E-2 Xe-1 31 m 5.4E+1 4.9E-6 2.6E-4 Xe-133 5.4E+1 1.1E-5 5.9E-4 Xe-135 5.4E+1 6.1E-5 3.3E-3 Ar-41 5.4E+1 2.9E-4 1.6E-2 The value of XQjAyi = 5.93E-2 D7 = 5.93E-2 x 5.8E-7 = 3.44-8 mRad Determining Noble Gas Beta Radiation Dose The beta air dose due to noble gases discharged from the plant shall be determined for the current calendar quarter and current calendar year at least once per 31 days. The beta air dose is calculated in the same manner as the gamma air dose using the beta air dose factors from Table 3.3-1 and Equation 3.3-3 or 3.3-4.

3 - 52 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.4: DOSE - IODINE-131, IODINE-133. TRITIUM, AND RADIOACTIVE MATERIAL IN PARTICULATE FORM 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 unit, to areas at and beyond the SITE BOUNDARY (see Figure 1.5-1) 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 131, Iodine 133, 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 Control 1.6.6, 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.

b. The provisions of Administrative Control section 1.6.3 are not applicable.

SURVEILLANCE REQUIREMENTS 3.4.1 Cumulative dose contributions for the current calendar quarter and current calendar year for Iodine 131, Iodine 133, tritium and radionuclides in particulate form with half-lives greater than 8 days shall be determined in accordance with the methodology and parameters in this ODCM at least once per 31 days.

CONTROL 3.4: DOSE - IODINE-131, IODINE-133. TRITIUM, AND RADIOACTIVE MATERIAL IN PARTICULATE FORM, (continued)

METHOD 3.4.1: DOSE DUE TO IODINE, TRITIUM, AND PARTICULATES INGASEOUS EFFLUENTS A. Determining the Quantity of Iodine, Tritium, and Particulates Radionuclides, other than noble gases, in gaseous effluents that are measured by the radioactive gaseous waste sampling and analysis program, described in ODCM Table 3.2-1, are used as the release term in dose calculations. Airborne releases are discharged either via a stack above the top of the containment building or via other vents and are treated as a mixed mode release from a single location. Releases of 3 - 53 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS steam from the secondary system concurrent with primary to secondary leakage will also result in the release of activity to the atmosphere. For steam generator blowdown, using a blowdown sample analysis, it is assumed that 5% of the 1-131 and 1-133 and 33% of the tritium in the blowdown stream become airborne with the remainder staying in the liquid phase. For other unmonitored releases, the quantity of airborne releases may be determined by performing a steam mass balance. For each of these release combinations, samples are analyzed weekly, monthly, quarterly, or for each batch releases according to Table 3.2-1 Each sample provides a measure of the concentration of specific radionuclides, Ci, in gaseous effluent discharged at flow rate, F, during a time increment, t. Thus, each release is quantified according to the relation Qik = Ck °Fj 9 tj Eqn 3.4-1 where:

Qik = the quantity of radionuclide i released in a given effluent stream based on a single analysis, k, (ptCi)

Cik = concentration of radionuclide i in a gaseous effluent identified by analysis, k, (p.Ci/cc)

Fj effluent stream discharge rate during time increment, tj, (cc/sec) t time increment, t, during which radionuclide i at concentration Cik is being discharged, (sec).

3 -54 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.4: DOSE - IODINE-131, IODINE-133. TRITIUM, AND RADIOACTIVE MATERIAL IN PARTICULATE FORM, (continued)

METHOD 3.4.1: DOSE DUE TO IODINE, TRITIUM, AND PARTICULATES INGASEOUS EFFLUENTS, (continued)

A. Determining the Quantity of Iodine, Tritium, and Particulates, (continued)

Note: A steam mass to determine other unmonitored releases may be determined using the following:

Fj = M, - (MI + M,)

where:

M = the measured mass of makeup water entering the secondary system during time interval, tj, (gm /sec).

M, = the measured mass of water discharged from the secondary system as liquid during time interval, tj, e.g. steam generator blowdown.

M = the measured mass of steam or non-condensable gases discharged from the secondary system during time interval, tj, e.g. air ejector discharge.

Note: It is assumed that all of the 1-131, 1-133, and tritium in the other unmonitored releases are discharged as airborne species. It also assumed that gm/sec is equivalent to cc/sec.

B. Calculating the Dose Due to Iodine, Tritium, and Particulates A person may be exposed directly to an airborne concentration of radioactive material discharged in an effluent gaseous stream and indirectly via pathways involving deposition of radioactive material onto the ground. Dose estimates should account for the exposure via the following pathways:

o direct radiation from airborne radionuclides (except noble gases) o inhalation o direct radiation from ground plane deposition o fruits and vegetables o air-grass-cow-meat o air-grass-cow-milk 3 -55 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.4: DOSE - IODINE-131, IODINE-133. TRITIUM, AND RADIOACTIVE MATERIAL IN PARTICULATE FORM, (continued)

METHOD 3.4.1: DOSE DUE TO IODINE, TRITIUM, AND PARTICULATES IN GASEOUS EFFLUENTS, (continued)

B. Calculating the Dose Due to Iodine, Tritium, and Particulates, (continued)

Of all these pathways, the air-grass-cow-milk pathway is by far the controlling dose contributor. The radioiodines contribute essentially all of the dose, by this pathway, with 1-131 typically contributing greater than 95%. The dose transfer factors for the radioiodines are much greater than for any of the other radionuclides. The critical organ is the infant's thyroid.

For this reason, the potential critical organ dose via airborne effluents can be estimated by determining an effective dose transfer factor for the radioiodines based on the typical radioactive effluent distribution, the air-grass-cow-milk pathway, and the infant thyroid as the receptor. Then for conservatism the total cumulative release of all radioiodines and particulates can be used along with the effective dose transfer factor to determine a conservative estimate of the infant thyroid dose.

Surveillance 3.4.1, requires an evaluation be performed once per 31 days to verify that the accumulated total body or organ dose for the current calendar quarter and calendar year does not exceed the limit as given in Control 3.4. Dose commitment due to iodine and particulates may be calculated by using the following equation:

3.17x10-8 D DMk = 3 -8.TG 131 eYXQ,k Eqn 3.4-2 0.8 Q where:

DMk = the dose commitment to an infant's thyroid received from exposure via the air-grass-cow-milk pathway and attributable to iodine identified in analysis k of effluent air, (mrem) 3.17 x 10-8 = conversion constant, (yr/sec) 0.8 = a conservatism factor which, in effect, increases the estimated dose to compensate for variability in the radionuclide distribution.

D/Q = relative deposition 2

rate onto ground from a mixed mode atmospheric release (m- )

3 -56 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 - RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.4: DOSE - IODINE-131. IODINE-133. TRITIUM, AND RADIOACTIVE MATERIAL IN PARTICULATE FORM, (continued)

METHOD 3.4.1: DOSE DUE TO IODINE, TRITIUM, AND PARTICULATES INGASEOUS EFFLUENTS, (continued)

B. Calculating the Dose Due to Iodine, Tritium, and Particulates, (continued)

TG131 = factor converting ground deposition of radioiodines to the dose commitment to an infant's thyroid exposed via the grass-cow-milk pathway, mrem/yr (jiCi/m 2 .sec)

Qik = the quantity of radionuclide, i (1-131 and 1-133), released in a given effluent stream based on a single analysis, k, (pLCi).

Surveillance 3.4.1 is satisfied by calculating the dose to an infant from iodine and particulates discharged as airborne effluents via the air-grass-cow-milk pathway and is evaluated by assuming a cow is on a pasture 4.5 miles west of the plant. (There are no milk or meat animals within 5 miles). At that location the reference atmospheric deposition factor is D/Q = 5 x 10 -10 m -2 When equation 3.4-2 is used to estimate the critical organ dose commitment, the effective dose transfer factor is:

TG131= 6.5 x 1011 mrem/vr (pjCi/m 2 .sec)

The reference data from which TG 131 was derived are summarized in Table 3C-2 of Appendix 3C.

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TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.4: DOSE - IODINE-131, IODINE-133. TRITIUM, AND RADIOACTIVE MATERIAL IN PARTICULATE FORM, (continued)

METHOD 3.4.11: DOSE DUE TO IODINE, TRITIUM, AND PARTICULATES IN GASEOUS EFFLUENTS, (continued)

B. Calculating the Dose Due to Iodine, Tritium, and Particulates, (continued)

Alternately, the requirement of Surveillance 3.4.1, to perform once per 31 days determinations of dose commitments due to radioiodine, tritium and radioactive particulates in effluent air may be made by using equations 3.4-3 through 3.4-5.

These equations are normally used when calculating doses for the Annual Radioactive Effluent Release Report.

The dose commitment from exposure to airborne concentrations of radioactive material other than noble gas from a release, Qik, via the inhalation and irradiation pathways is calculated with the equation D-k = 3.17x10 8 - Zd e XQ,R - YTAAp Y Eqn 3.4-3 Q p where:

Dank = the dose commitment to organ n of a person in age group a due to radionuclides identified in analysis k of an air effluent, (mrem).

3.17 x 10-8 = conversion constant, (yr/sec)

Xd/Q = atmospheric dispersion factor adjusted for depletion by deposition, (sec/m3).

Qik = the quantity of radionuclide i released in a given effluent stream based on analysis k, (pjCi).

TAanip = a factor converting airborne concentration of radionuclide i to dose commitment to organ n of a person in age group, a, where exposure is directly due to airborne material via pathway, p (inhalation, or external exposure to the plume),

mrem/yr ; (See Appendix 3B).

(pCi/m 3) 3 -58 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.4 DOSE - IODINE-131, IODINE-133. TRITIUM, AND RADIOACTIVE MATERIAL IN PARTICULATE FORM, (continued)

METHOD 3.4.1: DOSE DUE TO IODINE, TRITIUM, AND PARTICULATES IN GASEOUS EFFLUENTS, (continued)

B. Calculating the Dose Due to Iodine, Tritium, and Particulates, (continued)

The dose to a person from iodine and particulates discharged as airborne effluents via the inhalation and irradiation pathways is evaluated at the nearest garden, 3.6 miles west northwest of the plant. At that location, the reference atmospheric dispersion factor adjusted for depletion by deposition is Xd/Q = 1 x 10.7 sec/m3, (Table 3A-2).

The dose commitment via exposure pathways involving radionuclide deposition from the atmosphere onto vegetation or the ground is calculated with the equation D- =3.17x108 - D - ,Qik 9 YTGiP Eqn 3.4-4 Q i p where:

D/Q = relative deposition rate onto ground from a mixed mode atmospheric release, (m-2)

TGanip = factor converting ground deposition of radionuclide i to dose commitment to organ n of a person in age group a where exposure is due to radioactive material via pathway p (direct radiation from ground plane deposition, fruits and vegetables, air-grass-cow-meat, or air-grass-cow-milk), mrem/yr See Appendix 3B. (jtCi/m 2 -sec),

3 -59 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.4: DOSE - IODINE-131, IODINE-133. TRITIUM, AND RADIOACTIVE MATERIAL IN PARTICULATE FORM, (continued)

METHOD 3.4.11: DOSE DUE TO IODINE, TRITIUM, AND PARTICULATES IN GASEOUS EFFLUENTS, (continued) .

B. Calculating the Dose Due to Iodine, Tritium, and Particulates, (continued)

The dose to a person from iodine and particulates discharged as airborne effluents via the air-grass-cow-milk pathway is evaluated by assuming a cow is on a pasture 4.5 miles west of the plant.(There are no milk or meat animals within 5 miles). At this location, the reference atmospheric deposition factor is D/Q = 5 x 10 -10 m -2(Table 3A-3).

The concentration of tritium in vegetation is a function of the airborne concentration rather than the deposition. Thus, the dose commitment from airborne tritium via vegetation, (fruits and vegetables), air- grass-cow-milk, or air-grass-cow-meat pathways is calculated with the equation D,=3.17x10 8" _ Q

.~ X-Q,,

i 0* T Eqn 3.4-5 p

where:

X/Q = atmospheric dispersion factor at the off-site location of interest (sec/m3)

The dose to a person from tritium via the vegetation, (fruits and vegetables), air-grass-cow-milk, or air-grass-cow-meat pathways is evaluated at the nearest garden (with residence assumed) 3.6 miles west northwest of the plant. At that location, the reference atmospheric dispersion factor is X/Q = 1 x 10-7' sec/im 3.

3 -60 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.4: DOSE - IODINE-131, IODINE-133. TRITIUM, AND RADIOACTIVE MATERIAL IN PARTICULATE FORM, (continued)

METHOD 3.4.1: DOSE DUE TO IODINE, TRITIUM, AND PARTICULATES IN GASEOUS EFFLUENTS, (continued)

B. Calculating the Dose Due to Iodine, Tritium, and Particulates, (continued)

The dose commitment via a given pathway as a result of measured discharges from a release point is accumulated with D- YD k

Eqn 3.4-6 where:

Dan = the dose commitment to organ n of a person in age group, a.

k = the counting index; it may represent either:

p, analysis of a grab sample w, a weekly sample analysis m, a monthly composite analysis, or q, a quarterly composite analysis 3 -61 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE- GASEOUS EFFLUENTS CONTROL 3.4.: DOSE - IODINE 131, IODINE 133, TRITIUM, AND RADIOACTIVE MATERIAL IN PARTICULATE FORM, (continued)

BASIS 3.4: DOSE - IODINE 131, IODINE 133, TRITIUM, AND RADIOACTIVE MATERIAL IN PARTICULATE FORM This control applies to the release of radioactive materials in gaseous effluents from each unit at the site. For units with shared radwaste treatment systems, the gaseous effluents from the shared systems are proportioned among the units sharing that system.

This control is provided to implement the requirements of Appendix I, 10 CFR Part 50. The Control implements the guides set forth in Appendix I. The ACTION statements provide the required operating flexibility and at the same time implement the guides set forth in 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 calculation methods specified in the Surveillance Requirements implement the requirements in 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 specifications for lodinel 31, lodine-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 the 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 -62 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.4: DOSE - IODINE-131, IODINE-133. TRITIUM, AND RADIOACTIVE MATERIAL INPARTICULATE FORM, (continued)

EXAMPLE CALCULATIONS: Determining Dose Due to Iodine, Tritium, and Particulates Dose estimate should account for exposure of a person via the following pathways involving deposition of radioactivity on the ground.

direct radiation from airborne radionuclides except noble gases inhalation direct radiation from ground plane deposition fruits and vegetables air-grass-cow-meat air-grass-cow-milk The requirement to determine the dose commitments due to radioiodine, tritium, and radioactive particulates once per 31 days may be satisfied by using Equations 3.4-2, 3.4-3, 3.4-4, and 3.4-5.

Example:

Calculate the organ and total body dose to an infant from tritium inhalation and irradiation pathways and from radioiodine and particulates'via the grass-cow-milk pathway using Equations 3.4-4 and 3.4-5. The major non-noble gas activities released over a 31 day period were used for the calculation. The atmospheric dispersion factor and deposition rate values for a mixed mode release at 3.6 miles WNW and 4.5 miles west of the plant respectively were obtained from Tables 3A-2 and 3A-3. Factors TAanip and TGanip converting airborne activity to dose commitment are obtained from Appendix 3B for the organ, age group, and pathway.

For Iodine and Particulate:

D D-k =3.17x10-8 D-

1 Qk 1 TG-., Eqn 3.4-4 Q

p For Tritium; D.,k = 3.17x108- _ Y Qk Y_TAOP Eqn 3.4-5 Q p 3 -63 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS EXAMPLE CALCULATIONS: Determining Dose Due to Iodine, Tritium, and Particulates, (continued) where:

x/Q = atmospheric dispersion factor for a mixed mode release, (sec/m3).

D/Q = relative deposition rate onto ground from a mixed mode atmospheric release (m 2).

QOk = the quantity of radionuclide i released in a given effluent stream based on analysis k, (jtCi).

TAanip = a factor converting airborne concentration of radionuclide i to a dose commitment to organ n of a person in age group a where exposure is directly due to airborne material via pathway P (inhalation or external exposure to the plume), mrem/vr 3

(RCi/m ).

TGanip = factor converting ground deposition of radionuclide i to dose commitment to organ n of a person in age group a where exposure is due to radioactive material via pathway P (direct radiation from ground plane deposition, fruits and vegetables, air-grass-cow-meat, or air-grass-cow-milk) mrem/yr (VLCi/m 2 - sec)

Dank = the dose commitment to organ n of a person in age group a due to radionuclides identified in analysis k of an air effluent, (mrem).

The organ and total body dose to an infant from radioiodines and particulates via the grass-cow-milk pathway is shown in the following worksheet.

3 -64 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.4: DOSE - IODINE 131,133, TRITIUM, AND RADIOACTIVE MATERIAL IN PARTICULATE FORM, (continued)

EXAMPLE CALCULATIONS: ' Determining Dose Due to Iodine, Tritium, and Particulates, (continued)

GRASS-COW-MILK PATHWAY.

Organ Radionuclide Qik TGanp X/Q or D/Q 3.17E-8 D-k Total Dose Sum of D-k (mrem)

Bone H-3 2.OE+8 0 0 Co-58 2.0E+1 0 0 Co-60 1.7E+1 0 0 1-131 3.9E+3 2.59E+9 5E-10 3.17E-8 1.6E-4 Cs-1 37 6.1 E+1 6.44E+10 5E-10 3.17E-8 6.2E-5 2.2E-4 Liver H-3 2.0E+8 2.37E+3 1E-7 3.17E-8 1.5E-3 Co-58 2.0E+1 2.55E+7 5E-10 3.17E-8 8.1 E-9 Co-60 1.7E+1 8.73E+7 5E-10 3.17E-8 2,4E-8 1-131 3.9E+3 3.09E+9 5E-10 3.17E-8 1.9E-4 Cs-137 6.1 E+ 1 7.21E+10 5E-10 3.17E-8 7.0E-5 1.8E-3 Thyroid H-3 2.0E+8 2.37E+3 1E-7 3.17E-8 1.5E-3 Co-58 2.0E+1 0 Co-60 1.7E+1 0 1-131 3.9E+3 9.94E-11 5E-10 3.17E-8 6.1 E-1 Cs-137 6.1E+1 0 6.1E-1 3 - 65 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.4: DOSE - IODINE-131.133. TRITIUM. AND RADIOACTIVE MATERIAL IN PARTICULATE FORM.

(continued)

EXAMPLE CALCULATIONS: Determininq Dose Due to Iodine, Tritium, and Particulates, (continued)

GRASS-COW-MILK PATHWAY Organ Radionuclide Q~k TG-np X/Q or D/Q 3.17E-8 Dnk Total Dose Sum of D-k (mrem)

Kidney H-3 2.OE+8 1.04E+3 1E-7 3.17E-8 6.6E-4 Co-58 2.0E+1 0 Co-60 1.7E+1 0 1-131 3.9E+3 7.74E+8 5E-10 3.17E-8 4.8E-5 Cs-137 6.1E+1 3.66E+9 5E-10 3.17E-8 3.5E-6 7.1E-4 Lung H-3 2.OE+8 2.37E+3 1E-7 3.17E-8 1.5E-3 Co-58 2.0E+1 0 Co-60 1.7E+1 0 1-131 3.9E+3 0 Cs-137 6.1E+1 8.69E+9 5E-10 3.17E-8 8.4E-6 1.5E-3 GI/LI H-3 2.OE+8 2.37E+3 1E-7 3.17E-8 1.5E-3 Co-58 2.0E+1 6.6E+7 Co-60 1.7E+3 2.16E+8 1-131 3.9E+3 1.16E+8 Cs-1 37 6.1 E+1 1.86E+8 5E-10 3.17E-8 1.83E-7 1.5E-3 3 - 66 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.4: DOSE - IODINE-131,133. TRITIUM, AND RADIOACTIVE MATERIAL INPARTICULATE FORM, (continued)

EXAMPLE CALCULATIONS: Determininq Dose Due to Iodine, Tritium, and Particulates. (continued)

GRASS-COW-MILK PATHWAY Organ Radionuclide Qik TG-jQp X/ or DIQ 3.17E-8 Dak Total Dose Sum of D,.k (mrem)

Total Body H-3 2.OE+8 2.37E+3 1E-7 3.17E-8 1.5E-3 Co-58 2.0E+1 6.24E+7 Co-60 1.7E+3 2.09E+8 1-131 3.8E+3 1.81 E+9 Cs-137 6.1 E+1 4.14E+9 5E-7 3.17E-8 4.OE-6 1.5E-3 Skin H-3 2.OE+8 0 0 Co-58 2.0E+1 0 0 Co-60 1.7E+1 0 0 1-131 3.9E+3 0 0 Cs-137 6.1E+1 0 0 0 3 - 67 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.5: GASEOUS RADWASTE TREATMENT SYSTEM The VENTILATION EXHAUST TREATMENT SYSTEM and the GAS DECAY TANK SYSTEM shall be OPERABLE and appropriate portions of these systems shall be used to reduce releases of radioactivity when the projected doses in 31 days due to gaseous effluent releases, from each unit, to areas at and beyond the SITE BOUNDARY (see Figure 1.2-1) would exceed:

a. 0.2 mrad to air from gamma radiation, or

b. 0.4 mrad to air from beta radiation, or

c. 0.3 mrem to any organ of a MEMBER OF THE PUBLIC.

APPLICABILITY: At all times.

ACTION:

a. With radioactive gaseous waste being discharged without treatment and in excess of the above limits, prepare and submit to the Commission within 30 days, pursuant to Control 1.6.6, a Special Report that includes the following information:

1. Identification of any inoperable equipment or subsystems, and the reason for the inoperability,

2. Action(s) taken to restore the inoperable equipment to OPERABLE status, and

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

b. The provisions of Administrative Control section 1.6.3 are not applicable.

SURVEILLANCE REQUIREMENTS 3.5.1 Doses due to gaseous releases from each unit to areas at and beyond the SITE BOUNDARY shall be projected at least once per 31 days in accordance with the methodology and parameters in the ODCM when Gaseous Radwaste Treatment Systems are not being fully utilized.

3.5.2 The installed VENTILATION EXHAUST TREATMENT SYSTEM and GAS DECAY TANK SYSTEM shall be considered OPERABLE by meeting Controls 3.2 and either 3.3 or 3.4.

3 - 68 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS CONTROL 3.5: GASEOUS RADWASTE TREATMENT SYSTEM, (continued)

METHOD 3.5: PROJECTED DOSE FOR GASEOUS EFFLUENTS The monthly dose is normally projected by computing the dose accumulated during the most recent month and assuming the result represents the projected dose for the current month. The dose during the proceeding month will be computed as described in Methods 3.3.1, 3.3.2, and 3.4 Alternately, Control 3.5 is satisfied by extrapolating the dose to date during the current month to include the entire month. The dose to date is calculated as described in Methods 3.3.1, 3.3.2, and 3.4. This method may be used when a more accurate projection is required and sufficient data is available to make this determination.

The dose is projected with the relation:

P= .31 *D X Eqn 3.5-1 where:

P = the projected dose during the month, (mrem) 31 = number of days in a calendar month, (days)

X = number of days in current month to date represented by available radioactive effluent sample, (days)

D = dose to date during current month calculated according to Methods 3.3.1, 3.3.2, and 3.4 (mrem), i.e., gamma, beta, or organ dose respectively.

3 - 69 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS BASIS 3.5: GASEOUS RADWASTE TREATMENT SYSTEM This control applies to the release of radioactive materials in gaseous effluents from each unit at the site. For units with shared radwaste treatment systems, the gaseous effluents from the shared system are proportioned among the units sharing that system.

The OPERABILITY of the GAS DECAY TANK SYSTEM and the VENTILATION EXHAUST TREATMENT SYSTEM ensures that the systems 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 10 CFR 50.36a, General Design Criterion 60 of Appendix A to 10 CFR Part 50 and the 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 the dose objectives set forth in Appendix 1,10 CFR Part 50, for gaseous effluents.

3 - 70 11/22/02

APPENDIX 3A REFERENCE METEOROLOGY ANNUAL AVERAGE ATMOSPHERIC DISPERSION FACTORS

/

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS APPENDIX 3A

-REFERENCE METEOROLOGY ANNUAL AVERAGE ATMOSPHERIC DISPERSION FACTORS Contents Table Description Page 3A-1 Atmospheric Dispersion Factors (X/Q) 3A- 1 3A-2 Deposition Depleted Atmospheric Dispersion Factors (Xd /Q) 3A - 3 (gaseous releases corrected for depletion from the plume by fallout and deposition) 3A-3 Relative Deposition Rate (D/Q) 3A -5 (fraction of airborne release which is deposited on a square meter area of land)

Source of Data:

"Revised Radiological Effluent Technical Specifications: Gaseous Effluent Dilution Factors", Dames & Moore, November, 1978.

The data were compiled from observations during 01/01/76 to 12/31/77 Number of Valid Observations = 16538 Number of Invalid Observations = 1006 Number of Calms - Lower Level = 195 Number of Calms - Upper Level = 383 The factors include Terrain/Recirculation corrections and assume mixed mode releases.

3A- 1 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS Table 3A- 1 REFERENCE METEOROLOGY - ANNUAL AVERAGE ATMOSPHERIC DISPERSION FACTORS 3

X/Q sec/rM BASE DISTANCE IN MILES / KILOMETERS Mi .25 .75 .79 1.00 1.50 2.00 2.50 2.75 sector Km. .40 1.21 1.27 1.61 2.41 3.22 4.02 4.42 NNE 8.9E-07 1.9E-07 1.8E-07 1.4E-07 8.3E-08 6.2E-08 5.OE-08 4.4E-08 NE 6.9E-07 1.5E-07 1.5E-07 1.1E-07 6.3E-08 4.8E-08 3.8E-08 3.5E-08 ENE 8.4E-07 1.4E-07 1.4E-07 1.OE-07 7.5E-08 5.2E-08 3.9E-08 3.6E-08 E 8.6E-07 1.9E-07 1.7E-07 1.3E-07 9.1 E-08 6.3E-08 5.1 E-08 4.6E-08 ESE 6.6E-07 1.5E-07 1.4E-07 1.2E-07 7.9E-08 5.7E-08 4.5E-08 4.OE-08 SE 1.6E-06 2.8E-07 2.7E-07 1.9E-07 1.1E-07 7.8E-08 6.1 E-08 5.5E-08 SSE 4.9E-06 9.2E-07 8.7E-07 6.3E-07 3.6E-07 2.5E-07 1.8E-07 1.6E-07 S 2.9E-06 4.6E-07 4.2E-07 3.1 E-07 1.8E-07 1.3E-07 1.OE-07 9.5E-08 SSW 6.5E-07 1.6E-07 1.5E-07 1.1 E-07 6.5E-08 5.4E-08 4.6E-08 3.8E-08 SW 1.5E-06 3.2E-07 3.OE-07 2.3E-07 1.4E-07 1.OE-07 7.9E-08 6.9E-08 WSW 2.9E-06 6.3E-07 5.9E-07 4.3E-07 2.3E-07 1.7E-07 1.3E-07 1.0E-07 W 6.3E-06 1.3E-06 1.2E-06 9.0E-07 5.2E-07 3.5E-07 2.6E-07 2.3E-07 WNW 4.1 E-06 8.7E-07 8.1 E-07 5.9E-07 3.4E-07 2.3E-07 1.7E-07 1.6E-07 NW 2.7E-06 6.0E-07 5.6E-07 4.1E-07 2.4E-07 1.6E-07 1.2E-07 1.0E-07 NNW 1.4E-06 2.9E-07 2.7E-07 2.0E-07 1.2E-07 9.1 E-08 6.8E-08 6.1 E-08 N 9.5E-07 2.1E-07 1.9E-07 1.5E-07 8.5E-08 5.9E-08 4.5E-08 4.OE-08 3A - 2 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 30 RADIOACTIVE GASEOUS EFFLUENTS Table 3A - 1 REFERENCE METEOROLOGY - ANNUAL AVERAGE ATMOSPHERIC DISPERSION FACTORS 3

x/Q sec/M BASE DISTANCE IN MILES / KILOMETERS Mi. 3.50 4.30 4.50 5.00 5.50 7.00 9.00 11.00 sector Km. 5.63 6.92 7.24 8.04 8.85 11.26 14.48 17.70 NNE 3.OE-08 2.3E-08 2.2E-08 2.OE-08 1.9E-08 1.4E-08 9.8E-09 6.6E-09 NE 2.5E-08 2.1 E-08 2.1 E-08 1.6E-08 1.3E-08 1.OE-08 7.3E-09 5.4E-09 ENE 2.8E-08 2.4E-08 2.3E-08 2.OE-08 1.8E-08 1.3E-08 1.1 E-08 7.4E-09 E 3.6E-08 2.8E-08 2.7E-08 2.4E-08 2.2E-08 1.7E-08 1.3E-08 9.8E-09 ESE 2.9E-08 2.4E-08 2.3E-08 2.OE-08 1.9E-08 1.2E-08 1.1E-08 9.6E-09 SE 4.2E-08 3.1 E-08 3.0E-08 2.7E-08 2.6E-08 2.1 E-08 1.5E-08 1.3E-08 SSE 1.1E-07 9.4E-08 9.OE-08 7.9E-08 7.1 E-08 4.9E-08 3.5E-08 2.7E-08 S 7.8E-08 5.8E-08 5.4E-08 5.OE-08 4.6E-08 3.3E-08 2.3E-08 1.8E-08 SSW 2.4E-08 2.5E-08 2.6E-08 2.1 E-08 1.8E-08 1.4E-08 9.4E-09 7.1E-09 SW 4.9E-08 3.5E-08 3.2E-08 2.9E-08 2.7E-08 1.9E-08 1.4E-08 1.OE-08 WSW 7.6E-08 5.8E-08 5.5E-08 4.8E-08 4.2E-08 3.1 E-08 2.2E-08 1.8E-08 W 1.7E-07 1.3E-07 1.2E-07 1.0E-07 9.2E-08 6.6E-08 4.5E-08 3.5E-08 WNW 1.2E-07 8.6E-08 8.1 E-08 7.1 E-08 6.3E-08 4.2E-08 2.9E-08 2.3E-08 NW 7.6E-08 5.6E-08 5.1 E-08 4.7E-08 4.3E-08 3.2E-08 2.OE-08 1.5E-08 NNW 4.5E-08 3.2E-08 3.OE-08 2.6E-08 2.4E-08 1.5E-08 1.OE-08 8.3E-09 N 3.2E-08 2.3E-08 2.2E-08 2.OE-08 1.7E-08 1.3E-08 1.OE-08 7.2E-09 3A - 2 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS Table 3A - 2 REFERENCE METEOROLOGY - DEPOSITION DEPLETED ANNUAL AVERAGE ATMOSPHERIC DISPERSION FACTORS 3

Xd/Q sec m BASE DISTANCE IN MILES / KILOMETERS Mi. .25 .75 .79 1.00 1.50 2.00 2.50 2.75 sector Km. .40 1.21 1.27 1.61 2.41 3.22 4.02 4.42 NNE 8.7E-07 1.7E-07 1.6E-07 1.2E-07 7.3E-08 5.5E-08 4.4E-08 3.8E-08 NE 6.9E-07 1.4E-07 1.3E-07 9.4E-08 5.5E-08 4.2E-08 3.3E-08 3.OE-08 ENE 8.OE-07 1.2E-07 1.2E-07 9.1 E-08 6.5E-08 4.5E-08 3.4E-08 3.1 E-08 E 8.6E-07 1.7E-07 1.5E-07 1.2E-07 7.6E-08 5.5E-08 4.4E-08 3.9E-08 ESE 6.1E-07 1.3E-07 1.3E-07 1.OE-07 6.9E-08 5.OE-08 3.9E-08 3.4E-08 SE 1.5E-06 2.6E-07 2.4E-07 1.7E-07 9.5E-08 6.7E-08 5.2E-08 4.7E-08 SSE 4.7E-06 8.2E-07 7.7E-07 5.6E-07 3.1 E-07 2.2E-07 1.5E-07 1.3E-07 S 2.8E-06 4.2E-07 3.8E-07 2.7E-07 1.5E-07 1.1 E-07 8.5E-08 7.8E-08 SSW 6.1 E-07 1.4E-07 1.4E-07 9.6E-08 5.6E-08 4.7E-08 3.9E-08 3.2E-08 SW 1.3E-06 2.8E-07 2.7E-07 2.OE-07 1.3E-07 9.1 E-08 6.7E-08 5.9E-08 WSW 2.7E-06 5.6E-07 5.2E-07 3.8E-07 2.1 E-07 1.4E-07 1.OE-07 8.7E-08 W 5.9E-06 1.2E-06 1.1E-06 7.9E-07 4.4E-07 3.1 E-07 2.2E-07 2.OE-07 WNW 3.8E-06 7.7E-07 7.3E-07 5.1 E-07 2.9E-07 2.OE-07 1.5E-07 1.4E-07 NW 2.5E-06 5.4E-07 5.1 E-07 3.6E-07 2.1 E-07 1.4E-07 1.1E-07 8.9E-08 NNW 1.4E-06 2.6E-07 2.4E-07 1.8E-07 1.1E-07 7.7E-08 6.OE-08 5.4E-08 N 8.8E-07 1.9E-07 1.8E-07 1.3E-07 7.8E-08 5.2E-08 3.9E-08 3.5E-08 3A - 2 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS Table 3A - 2 REFERENCE METEOROLOGY - DEPOSITION DEPLETED ANNUAL AVERAGE ATMOSPHERIC DISPERSION FACTORS 3

Xd/Q sec/rM BASE DISTANCE IN MILES / KILOMETERS Mi. 3.50 4.30 4.50 5.00 5.50 7.00 9.00 11.00 sector Km. 5.63 6.92 7.24 8.04 8.85 11.26 14.48 17.70 NNE 2.7E-08 2.1 E-08 1.9E-08 1.8E-08 1.6E-08 1.2E-08 8.5E-09 6.OE-09 NE 2.2E-08 1.8E-08 1.7E-08 1.4E-08 1.2E-08 8.8E-09 6.3E-09 4.5E-09 ENE 2.4E-08 2.OE-08 2.0E-08 1.8E-08 1.6E-08 1.2E-08 9.0E-09 6.7E-09 E 3.1E-08 2.4E-08 2.4E-08 2.1E-08 1.9E-08 1.5E-08 1.1E-08 7.9E-09 ESE 2.5E-08 2.0E-08 2.OE-08 1.8E-08 1.6E-08 1.1 E-08 8.8E-09 8.3E-09 SE 3.4E-08 2.6E-08 2.4E-08 2.3E-08 2.1 E-08 1.7E-08 1.3E-08 1.0E-08 SSE 9.2E-08 7.7E-08 7.4E-08 6.4E-08 5.8E-08 3.8E-08 2.7E-08 2.1 E-08 S 6.4E-08 4.8E-08 4.4E-08 4.1 E-08 3.7E-08 2.6E-08 1.9E-08 1.3E-08 SSW 2.OE-08 2.2E-08 2.2E-08 1.8E-08 1.5E-08 1.2E-08 7.9E-09 5.7E-09 SW 4.2E-08 2.9E-08 2.7E-08 2.4E-08 2.3E-08 1.5E-08 1.1E-08 8.6E-09 WSW 6.4E-08 4.8E-08 4.6E-08 4.OE-08 3.5E-08 2.6E-08 1.8E-08 1.4E-08 W 1.4E-07 1.OE-07 9.9E-08 8.6E-08 7.6E-08 5.4E-08 3.7E-08 2.8E-08 WNW 9.8E-08 7A4E-08 7.OE-08 6.1 E-08 5.4E-08 3.6E-08 2.5E-08 2.OE-08 NW 6.8E-08 5.OE-08 4.5E-08 4.1 E-08 3.8E-08 2.8E-08 1.8E-08 1.3E-08 NNW 4.OE-08 2.8E-08 2.6E-08 2.3E-08 2.OE-08 1.3E-08 9.1 E-09 6.9E-09 N 2.8E-08 2.OE-08 1.9E-08 1.7E-08 1.5E-08 1.1E-08 8.7E-09 6.3E-09 3A - 2 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3*n RADI"ACTIVE (ASE(")S FFFI tJENTS Table 3A - 3 REFERENCE METEOROLOGY - ANNUAL AVERAGED RELATIVE DEPOSITION RATE D/Q 1/M2 BASE DISTANCE IN MILES / KILOMETERS Mi. .25 .75 .79 1.00 1.50 2.00 2.50 2.75 sector Km. .40 1.21 1.27 1.61 2.41 3.22 4.02 4.42 NNE 6.4E-09 1.5E-09 1.4E-09 9.6E-10 4.7E-10 2.8E-10 2.OE-10 1.6E-10 NE 3.5E-09 8.7E-10 B.E-10 5.6E-10 2.8E-10 1.8E-10 1.2E-10 1.1E-10 ENE 2.8E-09 5.1E-10 5.OE-10 3.6E-10 2.1E-10 1.2E-10 7.6E-11 6.4E-11 E 2.7E-09 6.6E-10 5.9E-10 4.3E-10 2.4E-10 1.5E-10 1.1E-10 8.8E-11 ESE 1.6E-09 4.2E-10 4.1 E-10 3.1E-10 1.9E-10 1.2E-10 7.7E-11 6.5E-11 SE 5.3E-09 1.2E-09 1.1 E-09 7.1 E-10 3.7E-10 2.3E-10 1.6E-10 1.3E-10 SSE 2.6E-08 5.2E-09 4.9E-09 3.4E-09 1.8E-09 1.1E-09 6.8E-10 5.8E-10 S 1.2E-08 2.1E-09 1.9E-09 1.4E-09 6.7E-10 4.4E-10 3.OE-10 2.7E-10 SSW 2.3E-09 7.2E-10 6.7E-10 4.5E-10 2.4E-10 1.7E-10 1.2E-10 9.7E-11 SW 1.1E-08 2.7E-09 2.5E-09 1.9E-09 1.OE-09 6.3E-10 4.3E-10 3.6E-10 WSW 2.3E-08 5.OE-09 4.6E-09 3.2E-09 1.5E-09 9.7E-10 6.1E-10 4.9E-10 W 5.7E-08 1.2E-08 1.1 E-09 7.4E-09 3.5E-09 2.2E-09 1.4E-09 1.2E-09 WNW 4.1 E-08 9.6E-09 8.7E-09 5.7E-09 2.7E-09 1.6E-09 1.OE-09 9.OE-10 NW 2.4E-08 6.2E-09 5.6E-09 3.7E-09 1.7E-09 9.5E-10 6.1E-10 5.OE-10 NNW 1.2E-08 3.OE-09 2.7E-09 1.8E-09 9.5E-10 5.4E-10 3.6E-10 3.OE-10 N 5.8E-09 1.6E-09 1.4E-09 1.OE-09 4.8E-10 2.7E-10 1.8E-10 1.5E-10 3A - 2 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL roy RADIOACTIVE GASEOUS EFFLUENTS 30 Table 3A - 3 REFERENCE METEOROLOGY - ANNUAL AVERAGED RELATIVE DEPOSITION RATE D/Q 1/M2 BASE DISTANCE IN MILES I KILOMETERS Mi. 3.50 4.30 4.50 5.00 5.50 7.00 9.00 11.00 sector Km. 5.63 6.92 7.24 8.04 8.85 11.26 14.48 17.70 NNE 9.1E-11 6.2E-11 5.5E-11 4.7E-11 4.1E-11 2.7E-11 1.6E-11 9.3E-12 NE 6.4E-11 4.6E-11 4.3E-11 3.2E-11 2.5E-11 1.7E-11 9.9E-12 6.2E-12 ENE 4.1E-11 3.OE-11 2.9E-11 2.3E-11 1.9E-11 1.2E-11 8.1 E-12 5.2E-12 E 5.8E-11 3.9E-11 3.7E-11 3.0E-11 2.5E-11 1.6E-11 1.0E-1I 6.6E-12 ESE 4.OE-1 1 2.8E-1 1 2.7E-1 1 2.2E-1 1 1.8E-1 1 1.0E-1 1 7.5E-12 5.8E-1 2 SE 9.OE-11 6.OE-11 5.4E-11 4.7E-11 4.2E-11 2.9E-11 1.8E-11 1.3E-11 SSE 3.5E-10 2.6E-10 2.5E-10 2.1 E-10 1.8E-10 1.0E-10 6.6E-11 4.5E-11 S 2.OE-10 1.3E-10 1.2E-10 1.OE-10 9.1E-11 5.8E-11 3.4E-11 2.3E-11 SSW 5.3E-11 4.8E-11 4.8E-11 3.6E-11 2.8E-11 2.OE-11 1.0E-11 6.6E-12 SW 2.3E-10 1.4E-10 1.2E-10 1.1E-10 9.6E-11 5.5E-11 3.5E-11 2.2E-11 WSW 3.2E-10 2.2E-10 2.OE-10 1.6E-10 1.4E-10 8.5E-11 5.5E-11 3.8E-11 W 7.6E-10 5.OE-10 4.9E-10 3.9E-10 3.3E-10 2.1E-10 1.2E-10 8.7E-11 WNW 5.7E-10 3.8E-10 3.4E-10 2.8E-10 2.4E-10 1.4E-10 8.8E-11 6.1 E-1I NW 3.1 E-10 2.0E-10 1.8E-10 1.5E-10 1.3E-10 8.5E-11 4.5E-11 3.2E-11 NNW 2.OE-10 1.2E-10 1.1E-10 8.8E-11 7.5E-11 4.2E-11 2.5E-11 1.8E-11 N 9.6E-11 6.5E-11 5.8E-11 4.8E-11 4.0E-11 2.5E-11 i.7E-11 1.1 E-11 3A - 2 11/22/02

APPENDIX 3B PATHWAY-DOSE TRANSFER FACTORS

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS APPENDIX 3B PATHWAY-DOSE TRANSFER FACTORS Environmental pathway transfer factors, usage factors, and dose commitment factors appropriate for each exposure pathway, age, and organ are combined into integrated environmental concentration-to-dose factors for each radionuclide. This appendix includes tables of values of the transfer factors calculated in accord with equations and values recommended in NUREG-01331 for individual environmental pathways. In the event a single, composite transfer factor is desired for a given organ and age group, it can be obtained by summing the factors for appropriate pathways.

Appropriate transfer factors from Appendix A are used in performing dose assessment calculations prescribed in the ODCM.

1. J. Boegli, et. al., eds., 1978, Preparation of Radiological Effluent Technical Specifications for Nudear Power Plants, NUREG-0133, USNRC, Office of Nuclear Reactor Regulation.

3B1-1 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - GROUND PLANE DEPOSITION AGE GROUP - ADULT NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 0. 0. 0. 0. 0. 0. 0.

C-14 0. 0. 0. 0. 0. 0. 0. 0.

P-32 0. 0. 0. 0. 0. 0. 0. 0.

CR-51 4.68E+06 4.68E+06 4.68E+06 4.68E+06 4.68E+06 4.68E+06 5.53E+06 4.68E+06 MN-54 1.38E+09 1.38E+09 1.38E+09 1.38E+09 1.38E+09 1.38E+09 1.62E+09 1.38E+09 FE-59 2.75E+08 2.75E+08 2.75E+08 2.75E+08 2.75E+08 2.75E+08 3.23E+08 2.75E+08 CO-57 1.89E+08 1.89E+08 1.89E+08 1.89E+08 1.89E+08 1.89E+08 2.08E+08 1.89E+08 CO-58 3.80E+08 3.80E+08 3.80E+08 3.80E+08 3.80E+08 3.80E+08 4.45E+08 3.80E+08 CO-60 2.15E+10 2.15E+10 2.15E+10 2.15E+10 2.15E+10 2.15E+10 2.52E+10 2.15E.10 NI-63 0. 0. 0. 0. 0. 0. 0. 0.

ZN-65 7.43E+08 7.43E+08 7.43E+08 7.43E+08 7.43E+08 7.43E+08 8.54E+08 7.43E+08 RB-86 9.01E+06 9.01E+06 9.01E+06 9.01E+06 9.01E+06 9.01E+06 1.03E+07 9.01E+06 SR-89 2.17E+04 2.17E+04 2.17E+04 2.17E+04 2.17E+04 2.17E+04 2.51E+04 2.17E+04 SR-90 5.35E+06 5.35E+06 5.35E+06 5.35E+06 5.35E+06 5.35E+06 6.33E+06 5.35E+06 Y-91 1.08E+06 1.08E+06 1.08E+06 1.08E+06 1.08E+06 1.08E+06 1.22E+06 1.08E+06 ZR-95 5.01E+08 5.01E+08 5.01E+08 5.01E+08 5.01E+08 5.01E+08 5.86E+08 5.01E+08 NB-95 1.36E+08 1.36E+08 1.36E+08 1.36E+08 1.36E+08 1.36E+08 1.61 E+08 1.36E+08 RU-103 1.10E+08 1.10E+08 1.10E+08 1.10E+08 1.10E+08 1.10E+08 1.28E+08 1.1OE+08 RU-106 4.19E+08 4.19E+08 4.19E+08 4.19E+08 4.19E+08 4.19E+08 5.03E+08 4.19E+08 AG-110M 3.58E+09 3.58E+09 3.58E+09 3.58E+09 3.58E+09 3.58E+09 4.17E+09 3.58E+09 CD-115M 0. 0. 0. 0. 0. 0. 0. 0.

BASED ON 1 gICi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, Xd/Q, AND D/Q.

3B -2 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - GROUND PLANE DEPOSITION AGE GROUP - ADULT NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 0. 0. 0. 0. 0. 0. 1.37E+06 0.

SN-126 5.16E+10 5.16E+10 5.16E+10 5.16E+10 5.16E+10 5.16E+10 5.76E+10 5.16E+10 SB-1 24 5.98E+08 5.98E+09 5.98E+08 5.98E+08 5.98E+08 5.98E+08 6.90E+08 5.98E+08 SB-1 25 2.30E+09 2.30E+09 2.30E+09 2.30E+09 2.30E+09 2.30E+09 2.59E+09 2.30E+09 TE-125M 1.55E+06 1.55E+06 1.55E+06 1.55E+06 1.55E+06 1.55E+06 2.13E+06 1.55E+06 TE-127M 8.79E+05 8.79E+05 8.79E+05 8.79E+05 8.79E+05 8.79E+05 9.74E+05 8.79E+05 TE-129M 3.85E+07 3.85E+07 3.85E+07 3.85E+07 3.85E+07 3.85E+07 4.52E+07 3.85E+07 1-130 5.53E+06 5.53E+06 5.53E+06 5.53E+06 5.53E+06 5.53E+06 6.71E+06 5.53E+06 1-131 1.72E+07 1.72E+07 1.72E+07 1.72E+07 1.72E+07 1.72E+07 2.09E+07 1.72E+07 1-132 1.25E+06 1.25E+06 1.25E+06 1.25E+06 1.25E+06 1.25E+06 1.47E+06 1.25E+06 1-133 2.48E+06 2.48E+06 2.48E+06 2.48E+06 2.48E+06 2.48E+06 3.01 E+06 2.48E+06 1-134 4.50E+05 4.50E+05 4.50E+05 4.50E+05 4.50E+05 4.50E+05 5.35E+05 4.50E+05 1-135 2.56E+06 2.56E+06 2.56E+06 2.56E+06 2.56E+06 2.56E+06 2.99E+06 2.56E+06 CS-134 6.99E+09 6.99E+09 6.99E+09 6.99E+09 6.99E+09 6.99E+09 8.15E+09 6.99E+09 CS-1 36 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.69E+08 1.49E+08 CS-137 1.03E+10 1.03E+10 1.03E+10 1.03E+10 1.03E+10 1.03E+10 1.20E+10 1.03E+10 BA-140 1.68E+08 1.68E+08 1.68E+08 1.68E+08 1.68E+08 1.68E+08 1.90E+08 1.68E+08 CE-141 1.37E+07 1.37E+07 1.37E+07 1.37E+07 1.37E+07 1.37E+07 1.54E+07 1.37E+07 CE-144 1.13E+08 1.13E+08 1.13E+08 1.13E+08 1.13E+08 1.13E+08 1.31E+08 1.13E+08 PR-143 0. 0. 3.58E+09 0. 0. 0. 0. 0.

ND-147 8.48E+06 8.48E+06 8.48E+06 8.48E+06 8.48E+06 8.48E+06 1.02E+07 8.48E+06 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR ,/Q, X/Q, AND D/Q.

3B - 3 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - GROUND PLANE DEPOSITION AGE GROUP - TEENAGER NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 0. 0. 0. 0. 0. 0. 0.

C-14 0. 0. 0. 0. 0. 0. 0. 0.

P-32 0. 0. 0. 0. 0. 0. 0. 0.

CR-51 4.68E+06 4.68E+06 4.68E+06 4.68E+06 4.68E+06 4.68E+06 5.53E+06 4.68E+06 MN-54 1.38E+09 1.38E+09 1.38E+09 1.38E+09 1.38E+09 1.38E+09 1.62E+09 1.38E+09 FE-59 2.75E+08 2.75E+08 2.75E+08 2.75E+08 2.75E+08 2.75E+08 3.23E+08 2.75E+08 CO-57 1.89E+08 1.89E+08 1.89E+08 1.89E+08 1.89E+08 1.89E+08 2.08E+08 1.89E+08 CO-58 3.80E+08 3.80E+08 3.80E+08 3.80E+08 3.80E+08 3.80E+08 4.45E+08 3.80E+08 CO-60 2.15E+10 2.15E+10 2.15E+10 2.15E+10 2.15E+10 2.15E+10 2.52E+10 2.15E+10 NI-63 0. 0. 0. 0. 0. 0. 0. 0.

ZN-65 7.43E+08 7.43E+08 7.43E+08 7.43E+08 7.43E+08 7.43E+08 8.54E+08 7.43E+08 RB-86 9.01E+06 9.01E+06 9.01E+06 9.01E+06 9.01E+06 9.01E+06 1.03E+07 9.01E+06 SR-89 2.17E+04 2.17E+04 2.17E+04 2.17E+04 2.17E+04 2.17E+04 2.51E+04 2.17E+04 SR-90 5.35E+06 5.35E+06 5.35E+06 5.35E+06 5.35E+06 5.35E+06 6.33E+06 5.35E+06 Y-91 1.08E+06 1.08E+06 1.08E+06 1.08E+06 1.08E+06 1.08E+06 1.22E+06 1.08E+06 ZR-95 5.01E+08 5.01E+08 5.01E+08 5.01E+08 5.01E+08 5.01E+08 5.86E+08 5.01E+08 NB-95 1.36E+08 1.36E+08 1.36E+08 1.36E+08 1.36E+08 1.36E+08 1.61 E+08 1.36E+08 RU-103 1.10E+08 1.10E+08 1.10E+08 1.10E+08 1.1OE+08 1.10E+08 1.28E+08 1.10E+08 RU-106 4.19E+08 4.19E+08 4.19E+08 4.19E+08 4.19E+08 4.19E+08 5.03E+08 4.19E+08 AG-110M 3.58E+09 3.58E+09 3.58E+09 3.58E+09 3.58E+09 3.58E+09 4.17E+09 3.58E+09 CD-115M 0. 0. 0. 0. 0. 0. 0. 0.

BASED ON 1 jiCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR ./Q, xJQ, AND D/Q.

3B -4 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - GROUND PLANE DEPOSITION AGE GROUP - TEENAGER NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 0. 0. 0. 0. 0. 0. 1.37E+06 0.

SN-126 5.16E+10 5.16E+10 5.16E+10 5.16E+10 5.16E+10 5.16E+l0 5.76E+l0 5.16E+10 SB-1 24 5.98E+08 5.98E+08 5.98E+08 5.98E+08 5.98E+08 5.98E+08 6.90E+08 5.98E+08 SB-1 25 2.30E+09 2.30E+09 2.30E+09 2.30E+09 2.30E+09 2.30E+09 2.59E+09 2.30E+09 TE-125M 1.55E+06 1.55E+06 1.55E+06 1.55E+06 1.55E+06 1.55E+06 2.13E+06 1.55E+06 TE-127M 8.79E+05 8.79E+05 8.79E+05 8.79E+05 8.79E+05 8.79E+05 9.74E+05 8.79E+05 TE-129M 3.85E+07 3.85E+07 3.85E+07 3.85E+07 3.85E+07 3.85E+07 4.52E+07 3.85E+07 1-130 5.53E+06 5.53E+06 5.53E+06 5.53E+06 5.53E+06 5.53E+06 6.71 E+06 5.53E+06 1-131 1.72E+07 1.72E+07 1.72E+07 1.72E+07 1.72E+07 1.72E+07 2.09E+07 1.72E+07 1-132 1.25E+06 1.25E+06 1.25E+06 1.25E+06 1.25E+06 1.25E+06 1.47E+06 1.25E+06 1-133 2.48E+06 2.48E+06 2.48E+06 2.48E+06 2.48E+06 2.48E+06 3.01 E+06 2.48E+06 1-134 4.50E+05 4.50E+05 4.50E+05 4.50E+05 4.50E+05 4.50E+05 5.35E+05 4.50E+05 1-135 2.56E+06 2.56E+06 2.56E+06 2.56E+06 2.56E+06 2.56E+06 2.99E+06 2.56E+06 CS-134 6.99E+09 6.99E+09 6.99E+09 6.99E+09 6.99E+09 6.99E+09 8.15E+09 6.99E+09 CS-1 36 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.69E+08 1.49E+08 CS-137 1.03E+10 1.03E+10 1.03E+10 1.03E+10 1.03E+10 1.03E+10 1.20E+10 1.03E+10 BA-140 1.68E+08 1.68E+08 1.68E+08 1.68E+08 1.68E+08 1.68E+08 1.90E+08 1.68E+08 CE-141 1.37E+07 1.37E+07 1.37E+07 1.37E+07 1.37E+07 1.37E+07 1.54E+07 1.37E+07 CE-144 1.13E+08 1.13E+08 1.13E+08 1.13E+08 1.13E+08 1.13E+08 1.31E+08 1.13E+08 PR-143 0. 0. 0. 0. 0. 0. 0. 0.

ND-147 8.48E+06 8.48E+06 8.48E+06 8.48E+06 8.48E+06 8.48E+06 1.02E+07 8.48E+06 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, XwQ, AND D/Q.

3B - 5 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - GROUND PLANE DEPOSITION AGE GROUP - CHILD NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 0. 0. 0. 0. 0. 0. 0.

C-14 0. 0. 0. 0. 0. 0. 0. 0.

P-32 0. 0. 0. 0. 0. 0. 0. 0.

CR-51 4.68E+06 4.68E+06 4.68E+06 4.68E+06 4.68E+06 4.68E+06 5.53E+06 4.68E+06 MN-54 1.38E+09 1.38E+09 1.38E+09 1.38E+09 1.38E+09 1.38E+09 1.62E+09 1.38E+09 FE-59 2.75E+08 2.75E+08 2.75E+08 2.75E+08 2.75E+08 2.75E+08 3.23E+08 2.75E+08 CO-57 1.89E+08 1.89E+08 1.89E+08 1.89E+08 1.89E+08 1.89E+08 2.08E+08 1.89E+08 CO-58 3.80E+08 3.80E+08 3.80E+08 3.80E+08 3.80E+08 3.80E+08 4.45E+08 3.80E+08 CO-60 2.15E+10 2.15E+10 2.15E+10 2.15E+10 2.15E+10 2.15E+10 2.52E+10 2.15E+10 NI-63 0. 0. 0. 0. 0. 0. 0. 0.

ZN-65 7.43E+08 7.43E+08 7.43E+08 7.43E+08 7.43E+08 7.43E+08 8.54E+08 7.43E+08 RB-86 9.01E+06 9.01E+06 9.01E+06 9.01E+06 9.01E+06 9.01E+06 1.03E+07 9.01E+06 SR-89 2.17E+04 2.17E+04 2.17E+04 2.17E+04 2.17E+04 2.17E+04 2.51E+04 2.17E+04 SR-90 5.35E+06 5.35E+06 5.35E+06 5.35E+06 5.35E+06 5.35E+06 6.33E+06 5.35E+06 Y-91 1.08E+06 1.08E+06 1.08E+06 1.08E+06 1.08E+06 1.08E+06 1.22E+06 1.08E+06 ZR-95 5.01E+08 5.01E+08 5.01E+08 5.01E+08 5.01E+08 5.01E+08 5.86E+08 5.01E+08 NB-95 1.36E+08 1.36E+08 1.36E+08 1.36E+08 1.36E+08 1.36E+08 1.61E+08 1.36E+08 RU-103 1.10E+08 1.10E+08 1.1OE+08 1.10E+08 1.10E+08 1.10E+08 1.28E+08 1.10E+08 RU-106 4.19E+08 4.19E+08 4.19E+08 4.19E+08 4.19E+08 4.19E+08 5.03E+08 4.19E+08 AG-11OM 3.58E+09 3.58E+09 3.58E+09 3.58E+09 3.58E+09 3.58E+09 4.17E+09 3.58E+09 CD-115M 0. 0. 0. 0. 0. 0. 0. 0.

BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR x/Q, XJQ, AND D/Q.

3B -6 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - GROUND PLANE DEPOSITION AGE GROUP - CHILD NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 0. 0. 0. 0. 0. 0. 1.37E+06 0.

SN-126 5.16E+10 5.16E+10 5.16E+10 5.16E+10 5.16E+10 5.16E+10 5.76E+10 5.16E+10 S1-124 5.98E+08 5.98E+08 5.98E+08 5.98E+08 5.98E+08 5.98E+08 6.90E+08 5.98E+08 S--125 2.30E+09 2.30E+09 2.30E+09 2.30E+09 2.30E+09 2.30E+09 2.59E+09 2.30E+09 TE-125M 1.55E+06 1.55E+06 1.55E+06 1.55E+06 1.55E+06 1.55E+06 2.13E+06 1.55E+06 TE-127M 8.79E+05 8.79E+05 8.79E+05 8.79E+05 8.79E+05 8.79E+05 9.74E+05 8.79E+05 TE-129M 3.85E+07 3.85E+07 3.85E+07 3.85E+07 3.85E+07 3.85E+07 4.52E+07 3.85E+07 1-130 5.53E+06 5.53E+06 5.53E+06 5.53E+06 5.53E+06 5.53E+06 6.71 E+06 5.53E+06 1-131 1.72E+07 1.72E+07 1.72E+07 1.72E+07 1.72E+07 1.72E+07 2.09E+07 1.72E+07 1-132 1.25E+06 1.25E+06 1.25E+06 1.25E+06 1.25E+06 1.25E+06 1.47E+06 1.25E+06 1-133 2.48E+06 2.48E+06 2.48E+06 2.48E+06 2.48E+06 2.48E+06 3.01 E+06 2.48E+06 1-134 4.50E+05 4.50E+05 4.50E+05 4.50E+05 4.50E+05 4.50E+05 5.35E+05 4.50E+05 1-135 2.56E+06 2.56E+06 2.56E+06 2.56E+06 2.56E+06 2.56E+06 2.99E+06 2.56E+06 CS-1 34 6.99E+09 6.99E+09 6.99E+09 6.99E+09 6.99E+09 6.99E+09 8.15E+09 6.99E+09 CS-1 36 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.69E+08 1.49E+08 CS-137 1.03E+10 1.03E+10 1.03E+10 1.03E+10 1.03E+10 1.03E+10 1.20E+10 1.03E+10 BA-140 1.68E+08 1.68E+08 1.68E+08 1.68E+08 1.68E+08 1.68E+08 1.90E+08 1.68E+08 CE-141 1.37E+07 1.37E+07 1.37E+07 1.37E+07 1.37E+07 1.37E+07 1.54E+07 1.37E+07 CE-144 1.13E+08 1.13E+08 1.13E+08 1.13E+08 1.13E+08 1.13E+08 1.31E+08 1.13E+08 PR-143 0. 0. 0. 0. 0. 0. 0. 0.

ND-147 8.48E+06 8.48E+06 8.48E+06 8.48E+06 8.48E+06 8.48E+06 1.02E+07 8.48E+06 BASED ON 1 1.Ci/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, XdtQ, AND D/Q.

3B - 7 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - GROUND PLANE DEPOSITION AGE GROUP - INFANT NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 0. 0. 0. 0. 0. 0. 0.

C-14 0. 0. 0. 0. 0. 0. 0. 0.

P-32 0. 0. 0. 0. 0. 0. 0. 0.

CR-51 4.68E+06 4.68E+06 4.68E+06 4.68E+06 4.68E+06 4.68E+06 5.53E+06 4.68E+06 MN-54 1.38E+09 1.38E+09 1.38E+09 1.38E+09 1.38E+09 1.38E+09 1.62E+09 1.38E+09 FE-59 2.75E+08 2.75E+08 2.75E+08 2.75E+08 2.75E+08 2.75E+08 3.23E+08 2.75E+08 CO-57 1.89E+08 1.89E+08 1.89E+08 1.89E+08 1.89E+08 1.89E+08 2.08E+08 1.89E+08 CO-58 3.80E+08 3.80E+08 3.80E+08 3.80E+08 3.80E+08' 3.80E+08 4.45E+08 3.80E+08 CO-60 2.15E+10 2.15E+10 2.15E+10 2.15E+10 2.15E+10 2.15E+10 2.52E+10 2.15E+10 NI-63 0. 0. 0. 0. 0. 0. 0. 0.

ZN-65 7.43E+08 7.43E+08 7.43E+08 7.43E+08. 7.43E+08 7.43E+08 8.54E+08 7.43E+08 RB-86 9.01E+06 9.01E+06 9.01E+06 9.01E+06 9.01E+06 9.01E+06 1.03E+07 9.01E+06 SR-89 2.17E+04 2.17E+04 2.17E+04 2.17E+04 2.17E+04 2.17E+04 2.51E+04 2.17E+04 SR-90 5.35E+06 5.35E+06 5.35E+06 5.35E+06 5.35E+06 5.35E+06 6.33E+06 5.35E+06 Y-91 1.08E+06 1.08E+06 1.08E+06 1.08E+06 1.08E+06 1.08E+06 1.22E+06 1.08E+06 ZR-95 5.01E+08 5.01E+08 5.01E+08 5.01E+08 5.01E+08 5.01E+08 5.86E+08 5.01E+08 NB-95 1.36E+08 1.36E+08 1.36E+08 1.36E+08 1.36E+08 1.36E+08 1.61 E+08 1.36E+08 RU-103 1.10E+08 1.10E+08 1.1OE+08 1.10E+08 1.10E+08 1.10E+08 1.28E+08 1.10E+08 RU-106 4.19E+08 4.19E+08 4.19E+08 4.19E+08 4.19E+08 4.19E+08 5.03E+08 4.19E+08 AG-1I0M 3.58E+09 3.58E+09 3.58E+09 3.58E+09 3.58E+09 3.58E+09 4.17E+09 3.58E+09 CD-115M 0. 0. 0. 0. 0. 0. 0. 0.

BASED ON 1 LCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, yJQ, AND D/Q.

3B - 8 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - GROUND PLANE DEPOSITION AGE GROUP - INFANT NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 0. 0. 0. 0. 0. 0. 1.37E+06 0.

SN-126 5.16E+10 5.16E+10 5.16E+10 5.16E+10 5.16E+10 5.16E+10 5.76E+10 5.16E+10 SB-1 24 5.98E+08 5.98E+08 5.98E+08 5.98E+08 5.98E+08 5.98E+08 6.90E+08 5.98E+08 SB-125 2.30E+09 2.30E+09 2.30E+09 2.30E+09 2.30E+09 2.30E+09 2.59E+09 2.30E+09 TE-125M 1.55E+06 1.55E+06 1.55E+06 1.55E+06 1.55E+06 1.55E+06 2.13E+06 1.55E+06 TE-127M 8.79E+05 8.79E+05 8.79E+05 8.79E+05 8.79E+05 8.79E+05 9.74E+05 8.79E+05 TE-129M 3.85E+07 3.85E+07 3.85E+07 3.85E+07 3.85E+07 3.85E+07 4.52E+07 3.85E+07 1-130 5.53E+06 5.53E+06 5.53E+06 5.53E+06 5.53E+06 5.53E+06 6.71 E+06 5.53E+06 1-131 1.72E+07 1.72E+07 1.72E+07 1.72E+07 1.72E+07 1.72E+07 2.09E+07 1.72E+07 1-132 1.25E+06 1.25E+06 1.25E+06 1.25E+06 1.25E+06 1.25E+06 1.47E+06 1.25E+06 1-133 2.48E+06 2.48E+06 2.48E+06 2.48E+06 2.48E+06 2.48E+06 3.01 E+06 2.48E+06 1-134 4.50E+05 4.50E+05 4.50E+05 4.50E+05 4.50E+05 4.50E+05 5.35E+05 4.50E+05 1-135 2.56E+06 2.56E+06 2.56E+06 2.56E+06 2.56E+06 2.56E+06 2.99E+06 2.56E+06 CS-1 34 6.99E+09 6.99E+09 6.99E+09 6.99E+09 6.99E+09 6.99E+09 8.15E+09 6.99E+09 CS-1 36 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.49E+08 1.69E+08 1.49E+08 CS-137 1.03E+10 1.03E+10 1.03E+10 1.03E+10 1.03E+10 1.03E+10 1.20E+10 1.03E+10 BA-140 1.68E+08 1.68E+08 1.68E+08 1.68E+08 1.68E+08 1.68E+08 1.90E+08 1.68E+08 CE-141 1.37E+07 1.37E+07 1.37E+07 1.37E+07 1.37E+07 1.37E+07 1.54E+07 1.37E+07 CE-144 1.13E+08 1.13E+08 1.13E+08 1.13E+08 1.13E+08 1.13E+08 1.31E+08 1.13E+08 PR-143 0. 0. 0. 0. 0. 0. 0. 0.

ND-147 8.48E+06 8.48E+06 8.48E+06 8.48E+06 8.48E+06 8.48E+06 1.02E+07 8.48E+06 BASED ON 1 p.Ci/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, xd/Q, AND D/Q.

3B1-9 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - INHALATION AGE GROUP -ADULT NUCLIDE ORGAN DOSE FACTORS (MREM/YR PER UCI/CU.METER)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 1.07E+03 1.07E+03 1.07E+03 1.07E+03 1.07E+03 0. 1.07E+03 C-14 1.82E+04 3.42E+04 3.42E+03 3.42E+03 3.42E+03 3.42E+03 0. 3.42E+03 P-32 1.32E+06 7.72E+04 0. 0. 0. 8.64E+04 0. 5.02E+04 CR-51 0. 0. 5.95E+01 2.28E+01 1.44E+04 3.32E+03 0. 1.00E+02 MN-54 0. 3.96E+04 0. 9.84E+03 1.40E+06 7.74E+04 0. 6.30E+03 FE-59 1.18E+04 2.78E+07 0. 0.. 1.02E+06 1.88E+05 0. 1.06E+04 CO-57 0. 6.92E+02 0. 0. 3.70E+05 3.14E+04 0. 6.71 E+02 CO-58 0. 1.58E+03 0. 0. 9.28E+05 1.06E+05 0. 2.07E+03 CO-60 0. 1.15E+04 0. 0. 5.98E+06 2.85E+05 0. 1.48E+04 NI-63 4.32E+05 3.14E+04 0. 0. 1.78E+05 1.34E+04 0. 1.45E+04 ZN-65 3.24E+04 1.03E+05 0. 6.90E+04 8.72E+05 5.34E+04 0. 4.66E+04 RB-86 0. 1.35E+05 0. 0. 0. 1.66E+04 0. 5.90E+04 SR-89 3.04E+05 0. 0. 0. 1.40E+06 3.50E+05 0. 8.72E+03 SR-90 9.92E+07 0. 0. 0. 9.60E+06 7.22E+05 0. 6.1OE+06 Y-91 4.62E+05 0. 0. 0. 1.70E+06 3.85E+05 0. 1.24E+04 ZR-95 1.07E+05 3.44E+04 0. 5.42E+04 1.78E+06 1.50E+05 0. 2.33E+04 NB-95 1.41 E+04 7.82E+03 0. 7.74E+03 5.06E+05 1.04E+05 0. 4.21E+03 RU-103 1.58E+03 0. 0. 5.83E+03 5.06E+05 1.10E+05 0. 6.58E+02 RU-106 6.91E+04 0. 0. 1.34E+05 9.44E+06 9.12E+05 0. 8.72E+03 AG-110M 1.08E+04 1.OOE+04 0. 1.97E+04 4.64E+06 3.02E+05 0. 5.94E+03 CD-115M 0. 1.97E+05 0. 1.50E+05 1.41E+06 3.84E+05 0. 6.36E+03 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q AND Xd/Q 3B - 10 11/22/02

N TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - INHALATION AGE GROUP - ADULT NUCLIDE ORGAN DOSE FACTORS (MREMIYR PER UCI/CUMETER)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 2.42E+05 5.33E+03 4.53E+03 0. 2.30E+06 3.14E+05 0. 7.86E+03 SN-126 1.26E+06 3.34E+04 9.84E+03 0. 9.36E+06 1.27E+05 0. 4.80E+04 SB-124 3.12E+04 5.89E+02 7.55E+01 0. 2.48E+06 4.06E+05 0. 1.24E+04 SB-125 6.61E+04 7.13E+02 5.87E+01 0. 2.20E+06 1.01E+05 0. 1.33E+04 TE-125M 3.42E+03 1.58E+03 1.05E+03 1.24E+04 3.14E+05 7.06E+04 0. 4.67E+02 TE-127M 1.26E+04 5.62E+03 3.29E+03 4.58E+04 9.60E+05 1.50E+05 0. 1.57E+03 TE-129M 9.76E+03 4.67E+03 3.44E+03 3.66E+04 1.16E+06 3.83E+05 0. 1.58E+03 1-130 4.58E+03 1.34E+04 1.74E+06 2.09E+04 0. 7.69E+03 0. 5.29E+03 1-131 2.52E+04 3.58E+04 1.19E+07 6.14E+04 0. 6.28E+03 0. 2.05E+04 1-132 1.16E+03 3.26E+03 4.38E+05 5.19E+03 0. 4.06E+02 0. 1.16E+03 1-133 8.64E+03 1.49E+04 2.93E+06 2.60E+04 0. 8.72E+03 0. 4.54E+03 1-134 6.45E+02 1.73E+03 2.30E+05 2.75E+03 0. 1.01 E+00 0. 6.16E+02 1-135 2.89E+03 6.99E+03 9.36E+05 1.11E+04 0. 5.25E+03 0. 2.58E+03 CS-134 3.74E+05 8.48E+05 0. 2.88E+05 9.76E+04 1.04E+04 0. 7.29E+05 CS-136 3.91E+04 1.46E+05 0. 8.56E+04 1.20E+04 1.17E+04 0. 1.11E+05 CS-1 37 4.78E+05 6.22E+05 0. 2.22E+05 7.53E+04 8.40E+03 0. 4.29E+05 BA-140 3.90E+04 4.90E+01 0. 1.67E+01 1.27E+06 2.18E+05 0. 2.57E+03 CE-141 1.99E+04 1.35E+04 0. 6.26E+03 3.62E+05 1.20E+05 0. 1.53E+03 CE-144 3.43E+06 1.43E+06 0. 8.48E+05 7.78E+06 8.16E+05 0. 1.84E+05 PR-143 9.36E+03 3.75E+03 0. 2.16E+03 2.81E+05 2.OOE+05 0. 4.63E+02 ND-147 5.27E+03 6.1OE+03 0. 3.56E+03 2.21E+05 1.73E+05 0. 3.65E+02 BASED ON 1 gCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR x/Q AND yXd/Q 3B- 11 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS -

ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - INHALATION AGE GROUP - TEENAGER NUCLIDE ORGAN DOSE FACTORS (MREM/R PER UCI/CU.METER)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 8.48E+02 8.48E+02 1.07E+03 8.48E+02 8.48E+02 0. 8.48E+02 C-14 4.58E+03 4.53E+03 4.53E+03 3.42E+03 4.53E+03 4.58E+03 0. 4.53E+03 P-32 1.32E+06 7.72E+04 0. 0. 0. 8.64E+04 0. 5.02E+04 CR-51 0. 0. 5.95E+01 2.28E+01 1.44E+04 3.32E+03 0. 1.OOE+02 MN-54 0. 3.96E+04 0. 9.84E+03 1.40E+06 7.74E+04 0. 6.30E+03 FE-59 1.18E+04 2.78E+07 0. 0. 1.02E+06 1.88E+05 0. 1.06E+04 CO-57 0. 6.92E+02 0. 0. 3.70E+05 3.14E+04 0. 6.71E+02 CO-58 0. 1.76E+02 0. 0. 1.37E+06 9.52E+04 0. 2.34E.02 CO-60 0. 1.24E+03 0. 0. 8.56E+06 2.35E+05 0. 1.65E+34 NI-63 4.32E+05 3.14E+04 0. 0. 1.78E+05 1.34E+04 0. 1.45E+04 ZN-65 3.24E+04 1.03E+05 0. 6.90E+04 8.72E+05 5.34E+04 0. 4.66E+04 RB-86 0. 1.35E+05 0. 0. 0. 1.66E+04 0. 5.90E+04 SR-89 3.37E+04 0. 0. 0.1 2.50E+06 3.54E+05 0. 1.11E+03 SR-90 1.18E+07 0. 0. 0. 1.66E+07 7.24E+05 0. 7.23E+05 Y-91 5.38E+04 0. 0. 0. 2.86E+06 3.74E+05 0. 1.44E+03 ZR-95 1.09E+04 3.663+03 0. 5.42E+04 2.56E+06 1.33E+05 0. 2.54E+03 NB-95 1.36E+03 8.24E+02 0. 7.74E+03 7.17E+05 8.80E+04 0. 4.62E+02 RU-103 1.63E+02 0. 0. 5.83E+03 7.51E+05 9.44E+04 0. 7.32E+01 RU-106 8.40E+03 0. 0. 1.34E+05 1.64E+07 9.28E+05 0. 1.06E+03 AG-110M 1.08E+04 1.OOE+04 0. 1.97E+04 4.64E+06 3.02E+05 0. 5.94E+03 CD-115M 0. 1.97E+05 0. 1.58E+05 1.41E+06 3.84E+05 0. 6.36E+03 BASED ON 1 ýtCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR x/Q AND Xd/Q.

3B - 12 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - INHALATION AGE GROUP - TEENAGER NUCLIDE ORGAN DOSE FACTORS (MREM/YR PER UCI/CU.METER)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 2.79E+04 6.14E+02 4.92E+02 0. 3.91E+06 3.13E+05 0. 9.20E+02 SN-126 1.26E+06 3.34E+04 9.84E+03 0. 9.36E+06 1.27E+05 0. 4.80E+04 SB-124 3.12E+04 5.89E+02 7.55E+01 0. 2.48E+06 4.06E+05 0. 1.24E+04 SB-125 6.61E+04 7.13E+02 5.87E+01 0. 2.20E+06 1.01E+05 0. 1.33E+04 TE-125M 4.07E+02 1.86E+02 1.17E+02 1.24E+04 5.36E+05 7.08E+04 0. 5.53E+01 TE-127M 1.26E+04 5.62E+03 3.29E+03 4.58E+04 9.60E+05 1.50E+05 0. 1.57E+03 TE-129M 1.19E+03 5.64E+02 3.90E+02 3.66E+04 2.03E+06 3.84E+05 0. 1.92E+02 1-130 4.58E+03 1.34E+04 1.74E+06 2.09E+04 0. 7.69E+03 0. 5.29E+03 1-131 3.37E+04 4.72E+04 1.39E+07 6.14E+04 0. 5.96E+03 0. 2.82E+04 1-132 1.16E+03 3.26E+03 4.38E+05 5.19E+03 0. 4.06E+02 0. 1.16E+03 1-133 1.23E+04 2.06E+04 3.83E+06 2.60E+04 0. 1.00E+04 0. 6.34E+03 1-134 6.45E+03 1.73E+03 2.30E+05 2.75E+03 0. 1.01E+00 0. 6.16E+02 1-135 2.69E+03 6.99E+03 9.36E+05 1.11E+04 0. 5.25E+03 0. 2.58E+03 CS-134 4.83E+05 1.10E+06 0. 2.88E+05 1.44E+05 8.96E+03 0. 5.44E+05 CS-136 3.91E+04 1.46E+05 0. 8.56E+04 1.20E+04 1.17E+04 0. 1.11E+05 CS-1 37 6.42E+05 8.24E+05 0. 2.22E+05 1.18E+05 7.68E+03 0. 3.03E+05 BA-140 5.30E+03 4.85E+00 0. 1.67E+01 2.02E+06 2.12E+04 0. 3.42E+02 CE-141 2.27E+03 1.52E+03 0. 6.26E+03 5.83E+05 1.14E+05 0. 1.74E+02 CE-144 4.19E+05 1.74E+05 0. 8.48E+05 1.38E+07 8.40E+05 0. 2.24E+04 PR-143 9.36E+03 3.75E+03 0. 2.16E+03 2.81E+05 2.OOE+05 0. 4.63E+02 ND-147 5.27E+03 6.1OE+03 0. 3.56E+03 2.21E+05 1.73E+05 0. 3.65E+02 BASED ON 1 giCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR ,/Q AND XdIQ.

3B - 13 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - INHALATION AGE GROUP - CHILD NUCLIDE ORGAN DOSE FACTORS (MREM/YR PER UCI/CUMETER)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 7.51E+02 7.51E+02 4.96E+02 7.51E+02 7.51E+02 0. 7.51E+02 C-14 6.25E+03 6.25E+03 6.25E+03 1.58E+03 6.25E+03 6.25E+03 0. 6.25E+03 P-32 6.11 E+05 3.57E+04 0. 0. 0. 4.00E+04 0. 2.32E+04 CR-51 0. 0. 2.75E+01 1.06E+01 6.66E+03 1.54E+03 0. 4.63E+01 MN-54 0. 1.83E+04 0. 4.55E+03 6.48E+05 3.58E+04 0. 2.91E+03 FE-59 5.44E+03 1.28E+07 0. 0. 4.70E+05 8.70E+04 0. 4.88E+03 CO-57 0. 3.20E+02 0. 0. 1.71E+05 1.45E+04 0. 3.10E+02 CO-58 0. 1.52E+02 0. 0. 1.13E+06 3.62E+04 0. 2.68E+02 CO-60 0. 1.07E+03 0. 0. 6.92E+06 9.36E+04 0. 1.88E+03 NI-63 2.OOE+05 1.45E+04 0. 0. 8.25E+04 6.18E+03 0. 6.70E+03 ZN-65 1.50E+04 4.77E+04 0. 3.19E+04 4.03E+05 2.47E+04 0. 2.15E+04 RB-86 0. 6.25E+04 0. 0. 0. 7.70E+03 0. 2.73E+04 SR-89 5.37E+04 0. 0. 0. 2.24E+06 1.69E+05 0. 1.54E+03 SR-90 1.64E+07 0. 0. 0. 1.48E+07 3.45E+05 0. 9.99E+05 Y-91 7.44E+04 0. 0. 0. 2.55E+06 1.78E+05 0. 1.98E+03 ZR-95 1.41E+04 3.28E+03 0. 2.51E+04 2.12E+06 5.74E+04 0. 2.98E+03 NB-95 1.70E+03 7.25E+02 0. 3.58E+03 5.85E+05 3.32E+04 0. 5.33E+02 RU-103 2.16E+02 0. 0. 2.70E+03 6.33E+05 4.22E+04 0. 8.73E+01 RU-106 1.15E+04 0. 0. 6.18E+04 1.45E+07 4.37E+05 0. 1.44E+03 AG-110M 5.00E+03 4.63E+03 0. 9.1OE+03 2.15E+06 1.40E+05 0. 2.75E+03 CD-115M 0. 9.10E+04 0. 7.33E+04 6.51E+05 1.78E+05 0. 2.94E+03 BASED ON 1 pjCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q AND XdQ.

3B - 14 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - INHALATION AGE GROUP - CHILD NUCLIDE ORGAN DOSE FACTORS (MREM/YR PER UCI/CU.METER)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 3.85E+04 6.44E+02 6.81E4-02 0. 3.50E+06 1.49E+05 0. 1.27E+03 SN-126 5.85E+05 1.55E+04 4.55E+03 0. 4.33E+06 5.88E+04 0. 2.22E+04 SB-124 1.44E+04 2.72E+02 3.49E+01 0. 1.15E+06 1.88E+05 0. 5.74E+03 SB-125 3.06E+04 3.30E+02 2.72E+01 0. 1.02E+06 4.66E+04 0. 6.14E+03 TE-125M 5.62E+02 1.94E+02 1.61 E+02 5.74E+03 4.81 E+05 3.38E+04 0. 7.62E+01 TE-127M 5.85E+03 2.60E+03 1.52E+03 2.12E+04 4.44E+05 6.92E+04 0. 7.25E+02 TE-129M 1.64E+03 5.85E+02 5.40E+02 1.69E+04 1.80E+06 1.82E+05 0. 2.60E+02 1-130 2.12E+03 6.22E+03 8.07E+05 9.66E+03 0. 3.56E+03 0. 2.45E+03 1-131 4.55E+04 4.63E+04 1.54E+07 2.84E+04 0. 2.65E+03 0. 3.50E+04 1-132 5.37E+02 1.51 E+03 2.03E+05 2.40E+03 0. 1.88E+02 0. 5.37E+02 1-133 1.68E+04 2.05E+04 5.03E+06 1.20E+04 0. 5.55E+03 0. 8.03E+02 1-134 2.98E+02 7.99E+02 1.06E+05 1.27E+03 0. 4.66E-01 0. 2.85E+02 1-135 1.24E+03 3.23E+03 4.33E+05 5.14E+03 0. 2.43E+03 0. 1.19E+03 CS-134 6.22E+05 9.95E+05 0. 1.33E+05 1.19E+05 3.77E+03 0. 2.23E+05 CS-136 1.81E+04 6.77E+04 0. 3.96E+04 5.55E+03 5.40E+03 0. 5.14E+04 CS-1 37 8.66E+05 7.99E+05 0. 1.03E+05 1.00E+05 3.41 E+03 0. 1.25E+05 BA-140 7.14E+03 4.66E+00 0. 7.73E+00 1.74E+06 9.92E+03 0. 4.22E+02 CE-141 3.13E+03 1.57E+03 0. 2.90E+03 5.14E+05 5.44E+04 0. 2.33E+02 CE-144 5.81E+05 1.82E+05 0. 3.92E+05 1.23E+07 4.OOE+05 0. 3.10E+04 PR-143 4.33E+03 1.74E+03 0. 9.99E+02 1.30E+05 9.25E+04 0. 2.14E+02 ND-147 2.44E+03 2.82E+03 0. 1.65E+03 1.02E+05 7.99E+04 0. 1.69E+02 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q AND XdaQ.

ý,,.313B - 15 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - INHALATION AGE GROUP - INFANT NUCLIDE ORGAN DOSE FACTORS (MREM/YR PER UCI/CU.METER)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 4.30E+02 4.30E+02 1.88E+02 4.30E+02 4.30E+02 0. 4.30E+02 C-14 5.04E+03 4.28E+03 4.28E+03 5.98E+02 4.28E+03 4.28E+03 0. 4.28E+03 P-32 2.31 E+05 1.35E+04 0. 0. 0. 1.51 E+04 0. 8.78E+03 CR-51 0. 0. 1.94E+01 3.99E+00 2.52E+03 5.81E+02 0. 1.75E+01 MN-54 0. 6.93E+03 0. 1.72E+03 2.45E+05 1.35E+04 0. 1.10E+03 FE-59 2.06E+03 4.86E+06 0. 0. 1.78E+05 3.29E+04 0. 1.85E+03 CO-57 0. 1.21E+02 0. 0. 6.47E+04 5.50E+03 0. 1.18E+02 CO-58 0. 1.18E+02 0. 0. 8.79E+05 1.21E+04 0. 1.68E+02 CO-60 0. 8.40E+02 0. 0. 5.57E+06 3.28E+04 0. 1.17E+03 NI-63 7.56E+04 5.49E+03 0. 0. 3.12E+04 2.34E+03 0. 2.53E+03 ZN-65 5.67E+03 1.81E+04 0. 1.21E+04 1.53E+05 9.35E+03 0. 8.15E+03 RB-86 0. 2.37E+04 0. 0. 0. 2.91 E+03 0. 1.03E+04 SR-89 4.31E+04 0. 0. 0. 2.31E+06 6.80E+04 0. 1.24E+03 SR-90 1.32E+07 0. 0. 0. 1.53E+07 1.39E+05 0. 8.06E+05 Y-91 5.98E+04 0. 0. 0. 2.63E+06 7.17E+04 0. 1.60E+03 ZR-95 1.08E+04 2.73E+03 0. 9.48E+03 1.81E+06 1.41E+04 0. 1.95E+03 NB-95 1.28E+03 5.75E+02 0. 1.35E+03 4.77E+05 1.21 E+04 0. 3.37E+02 RU-103 1.69E+02 0. 0. 1.02E+03 5.66E+05 1.58E+04 0. 5.85E+01 RU-106 9.31E+03 0. 0. 2.34E+04 1.50E+07 1.76E+05 0. 1.14E+03 AG-110M 1.89E+03 1.75E+03 0. 3.44E+03 8.12E+05 5.29E+04 0. 1.04E+03 CD-115M 0. 3.44E+04 0. 2.77E+04 2.46E+05 6.72E+04 0. 1.11E+03 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR x/Q AND X/JQ.

3B- 16 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - INHALATION AGE GROUP - INFANT NUCLIDE ORGAN DOSE FACTORS (MREM/YR PER UCI/CU.METER)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 3.11E+04 6.45E+02 6.45E+02 0. 3.61E+06 5.99E+04 0. 1.02E+03 SN-126 2.21E+05 5.85E+03 1.72E+03 0. 1.64E+06 2.23E+04 0. 8.40E+03 SB-124 5.46E+03 1.03E+02 1.32E+01 0. 4.34E+05 7.11E+04 0. 2.17E+03 SB-125 1.16E+04 1.25E+02 1.03E+01 0. 3.85E+05 1.76E+04 0. 2.32E+03 TE-125M 4.54E+02 1.95E+02 1.53E+02 2.17E+03 4.96E+05 1.36E+04 0. 6.16E+01 TE-127M 2.21 E+03 9.83E+02 5.75E+02 8.01 E+03 1.68E+05 2.62E+04 0. 2.74E+02 TE-129M 1.32E+03 5.80E+02 5.08E+02 6.40E+03 1.83E+06 7.32E+04 0. 2.06E+02 1-130 8.02E+02 2.35E+03 3.05E+05 3.65E+03 0. 1.35E+03 0. 9.25E+02 1-131 3.63E+04 4.27E+04 1.41 E+07 1.07E+04 0. 1.07E+03 0. 2.51E+04 1-132 2.03E+02 5.70E+02 7.67E+04 9.09E+02 0. 7.11E+01 0. 2.03E+02 1-133 1.34E+04 1.93E+04 4.66E+06 4.55E+03 0. 2.28E+03 0. 5.87E+03 1-134 1.13E+02 3.02E+02 4.02E+04 4.82E+02 0. 1.76E-01 0. 1.08E+02 1-135 4.70E+02 1.22E+03 1.64E+05 1.95E+03 0. 9.18E+02 0. 4.51E+02 CS-134 4.80E+05 8.25E+05 0. 5.04E+04 1.01E+05 1.37E+03 0. 7.32E+04 CS-136 6.85E+03 2.56E+04 0. 1.50E+04 2.1OE+03 2.04E+03 0. 1.95E+04 CS-137 6.86E+05 7.31E+05 0. 3.89E+04 9.45E+04 1.32E+03 0. 4.41E+04 BA-140 5.70E+03 4.27E+00 0. 2.93E+00 1.64E+06 3.88E+03 0. 2.95E+02 CE-141 2.52E+03 1.55E+03 0. 1.10E+03 5.24E+05 2.06E+04 0. 1.81E+02 CE-144 4.68E+05 1.82E+05 0. 1.48E+05 1.27E+07 1.61 E+05 0. 2.49E+04 PR-143 1.64E+03 6.57E+02 0. 3.78E+02 4.91E+04 3.50E+04 0: 8.11E+01 ND-147 9.28E+02 1.07E+03 0. 6.28E+02 3.86E+04 3.02E+04 0. 6.38E+01 BASED ON 1 pICi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q AND XjQ.

3B - 17 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-COW-MEAT (CONTAMINATED FORAGE) AGE GROUP - ADULT NUCLIDE ORGAN DOSE FACTOR (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 4.13E+02 4.13E+02 4.13E+02 4.13E+02 4.13E+02 0. 4.13E+02 C-14 3.33E+05 6.67E+04 6.67E+04 6.67E+04 6.67E+04 6.67E+04 0. 6.67E+04 P-32 4.67E+09 2.93E+08 0. 0. 0. 5.25E+08 0. 1.81E+08 CR-51 0. 0. 4.23E+03 1.56E+03 9.38E+03 1.78E+06 0. 7.07E+03 MN-54 0. 9.18E+06 0. 2.73E+06 0. 2.81E+07 0. 1.75E+06 FE-59 2.67E+08 6.33E+08 0. 0. 1.76E+08 2.09E+09 0. 2.41E+08 CO-57 0. 5.64E+06 0. 0. 0. 1.43E+08 0. 9.38E+06 CO-58 0. 1.83E+07 0. 0. 0. 3.70E+08 0. 4.09E+07 CO-60 0. 7.55E+07 0. 0. 0. 1.41 E+09 0. 1.66E+08 NI-63 1.89E+09 1.31 E+08 0. 0. 0. 2.73E+07 0. 6.33E+07 ZN-65 3.56E+08 1.13E+09 0. 7.57E+08 0. 7.13E+08 0. 5.12E+08 RB-86 0. 4.89E+08 0. 0. 0. 9.64E+07 0. 2.28E+08 SR-89 3.03E+08 0. 0. 0. 0. 4.84E+07 0. 8.67E+06 SR-90 1.25E+10 0. 0. 0. 0. 1.45E+09 0. 3.05E+09 Y-91 1.14E+06 0. 0. 0. 0. 6.26E+08 0. 3.05E+04 ZR-95 3.78E+06 1.67E+06 0. 2.01 E+06 0. 8.30E+09 0. 8.26E+05 NB-95 2.30E+06 1.20E+06 0. 1.27E+06 0. 7.75E+09 0. 5.02E+05 RU-103 1.06E+08 0. 0. 4.06E+08 0. 1.24E+10 0. 4.59E+07 RU-106 2.80E+09 0. 0. 5.41E+09 0. 1.81E+11 0. 3.54E+08 AG-110M 6.71E+06 6.21E+06 0. 1.22E+07 0. 2.53E+09 0. 3.69E+06 CD-115M 0. 1.46E+06 0. 1.16E+06 0. 6.15E+07 0. 4.67E+04 BASED ON 1 p.Ci/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR XIQ, XJQ, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3 - 18 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-COW-MEAT (CONTAMINATED FORAGE) AGE GROUP - ADULT NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 0. 0. 0. 0. 0. 0. 0. 0.

SN-126 1.86E+10 3.69E+08 1.08E+08 0. 6.46E+06 6.19E+09 0. 5.33E+08 SB-124 1.99E+07 3.75E+05 4.80E+04 0. 1.54E+07 5.62E+08 0. 7.85E+06 SB-125 6.65E+07 1.58E+07 1.29E+07 1.74E+08 2.49E+09 3.80E+08 0. 1.05E+07 TE-125M 3.59E+08 1.30E+08 1.08E+08 1.46E+09 0. 1.43E+09 0. 4.81E+07 TE-127M 1.13E+09 3.93E+08 2.96E+08 4.56E+09 0. 5.11E+09 0. 1.39E+08 TE-129M 1.14E+09 4.29E+08 3.95E+08 4.79E+09 0. 5.76E+09 0. 1.82E+08 1-130 2.38E-06 7.05E-06 8.96E-04 1.1OE-05 0. 6.04E-06 0. 2.77E-06 1-131 1.08E+07 1.55E+07 5.06E+09 2.65E+07 0. 4,07E+06 0. 8.85E+06 I-132 0. 0. 0. 0. 0. 0. 0. 0.

I-133 4.40E-01 7.63E-01 1.47E+02 1.33E+00 0. 6.71E-01 0. 2.33E-01 1-134 0. 0. 0. 0. 0. 0. 0. 0.

1-135 8.60E-02 7.94E-02 0. 3.01 E-02 9.04E-03 1.86E-03 0. 3.53E-02 CS-134 6.58E+08 1.57E+09 0. 5.08E+08 1.68E+08 2.74E+07 0. 1.28E+09 CS-136 1.18E+07 4.67E+07 0. 2.60E+07 3.56E+06 5.31E+06 0. 3.36E+07 CS-137 8.73E+08 1.19E+09 0. 4.06E+08 1.35E+08 2.30E+07 0. 7.82E+08 BA-140 2.88E+07 3.63E+04 0. 1.23E+04 2.07E+04 6.87E+07 0. 1.90E+06 CE-141 1.41 E+04 9.52E+03 0. 4.41E+03 0. 3.63E+07 0. 1.08E+03 CE-144 1.46E+06 6.1OE+05 0. 3.62E+05 0. 4.93E+08 0. 7.83E+04 PR-143 2.13E+04 8.57E+03 0. 4.94E+03 0. 9.34E+07 0. 1.06E+03 ND-147 1.72E+04 9.29E+03 0. 6.64E+03 0. 4.13E+07 0. 8.76E+02 BASED ON 1 j.Ci/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR x/Q, XJQ, AND D/Q.

NOTE -THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B- 19 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-COW-MEAT (CONTAMINATED FORAGE) AGE GROUP - TEENAGER NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 1.93E+02 1.93E+02 2.44E+02 1.93E+02 1.93E+02 0. 1.93E+02 C-14 5.23E+04 5.23E+04 5.23E+04 3.94E+04 5.23E+04 5.23E+04 0. 5.23E+04 P-32 2.76E+09 1.73E+08 0. 0. 0. 3.10E+08 0. 1.07E+08 CR-51 0. 0. 2.50E+02 9.22E+02 5.55E+03 1.05E+06 0. 4.18E+03 MN-54 0. 5.42E+06 0. 1.61E+06 0. 1.66E+07 0. 1.04E+06 FE-59 1.58E+08 3.74E+08 0. 0. 1.04E+08 1.24E+09 0. 1.42E+08 CO-57 0. 3.33E+06 0. 0. 0. 8.45E+07 0. 5.54E+06 CO-58 0. 1.44E+07 0. 0. 0. 1.94E+08 0. 3.27E+07 CO-60 0. 5.73E+07 0. 0. 0. 6.87E+08 0. 1.31E+08 NI-63 1.12E+09 7.74E+07 0. 0. 0. 1.61E+07 0. 3.74E+07 ZN-65 2.11E+08 6.69E+08 0. 4.47E+08 0. 4.21E+08 0. 3.03E+08 RB-86 0. 2.89E+08 0. 0. 0. 5.69E+07 0. 1.35E+08 SR-89 2.66E+08 0. 0. 0. 0. 2.89E+07 0. 7.64E+06 SR-90 1.01E+10 0. 0. 0. 2.79E+08 1.02E+09 0. 2.49E+09 Y-91 9.34E+05 0. 0. 0. 0. 3.59E+08 0. 2.49E+04 ZR-95 2.67E+06 1.24E+06 0. 1.18E+06 0. 4.20E+09 0. 7.61E+05 NB-95 1.58E+05 9.51 E+05 0. 7.48E+05 0. 3.88E+09 0. 5.37E+05 RU-103 8.05E+07 0. 0. 2.40E+08 0. 6.28E+09 0. 3.60E+07 RU-106 2.40E+09 0. 0. 3.20E+09 0. 1.09E+11 0. 3.02E+08 AG-11OM 3.97E+06 3.67E+06 0. 7.21E+06 0. 1.50E+09 0. 2.18E+06 CD-115M 0. 8.64E+05 0. 6.85E+05 0. 3.63E+07 0. 2.76E+04 BASED ON 1 pCi/SEC 1 RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, XJQ, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREMNR PER UCI/CU.METER) 3B - 20 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-COW-MEAT (CONTAMINATED FORAGE) AGE GROUP - TEENAGER NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 0. 0. 0. 0. 0. 0. 0. 0.

SN-126 1.10E+10 2.18E+08 6.38E+07 0. 3.82E+06 3.66E+09 0. 3.14E+08 SB-124 1.17E+07 2.21E+05 2.84E+04 0. 9.11E+06 3.32E+08 0. 4.64E+06 SB-125 5.01E+07 1.31E+07 1.02E+07 1.03E+08 1.47E+09 2.25E+08 0. 7.60E+06 TE-125M 3.03E+08 1.08E+08 8.55E+07 8.63E+08 0. 8.47E+08 0. 4.02E+07 TE-127M 6.60E+08 2.34E+08 1.77E+08 2.69E+09 0. 3.35E+09 0. 8.28E+07 TE-129M 9.78E+08 3.63E+08 3.13E+08 2.83E+09 0. 3.41E+09 0. 1.53E+08 1-130 1.41E-06 4.16E-06 5.30E-04 6.47E-06 0. 3.57E-06 0. 1.64E-06 1-131 8.54E+06 1.21 E+07 3.48E+09 1.56E+07 0. 2.28E+06 0. 7.19E+06 1-132 0. 0. 0. 0. 0. 0. 0. 0.

1-133 3.69E-01 6.26E-01 1.14E+02 7.88E-01 0. 4.55E-01 0. 1.93E-01 1-134 0. 0. 0. 0. 0. 0. 0. 0.

1-135 5.08E-02 4.69E-02 0. 1.78E-02 5.34E-03 1.10E-03 0. 2.08E-02 CS-1 34 5.03E+08 1.21 E+09 0. 3.OOE+08 1.47E+08 1.40E+07 0. 5.66E+08 CS-136 6.99E+06 2.76E+07 0. 1.54E+07 2.11E+06 3.14E+06 0. 1.99E+07 CS-137 6.92E+08 9.31E+08 0. 2.40E+08 1.24E+08 1.24E+07 0. 3.27E+08 BA-140 2.37E+07 2.93E+04 0. 7.20E+04 1.95E+04 9.19E+06 0. 1.53E+06 CE-141 1.12E+04 7.51E+03 0. 2.61E+03 0. 2.03E+07 0. 8.61E+02 CE-144 1.28E+06 5.23E+05 0. 2.14E+05 0. 3.OOE+08 0. 6.76E+04 PR-143 1.26E+04 5.07E+03 0. 2.92E+03 0. 5.52E+07 0. 6.26E+02 ND-147 1.01E+04 5.49E+03 0. 3.92E+03 0. 2.44E+07 0. 5.18E+02 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR x/Q, XJQ, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B - 21 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL

-3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-COW-MEAT (CONTAMINATED FORAGE) AGE GROUP - CHILD NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID ,,KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 2.33E+02 2.33E+02 1.54E+02 2.33E+02 2.33E+02 0. 2.33E+02 C-14 9.87E+04 9.87E+04 9.87E+04 2.49E+04- 9.87E+04 9.87E+04 0. 9.87E+04 P-32 1.74E+09 1.09E+08 0. 0. 0. 1.96E+08 0. 6.73E+07 CR-51 0. 0. 1.58E+03 5.82E+02 3.50E+03 6.63E+05 0. 2.64E+03 MN-54 0. 3.42E+06 0. 1.02E+06 0. 1.05E+07 0. 6.54E+05 FE-59 9.95E+07 2.37E+08 0. 0'.. 6.55E+07 7.79E+08 0. 8.93E+07 CO-57 0. 2.1OE+06 0. 0.' 0. 5.33E+07 0. 3.50E+06 CO-58 0. 1.69E+07 0. 0.i" 0. 1.OOE+08 0. 5.1OE+07 CO-60 0. 6.77E+07 0. 0.ý, 0. 3.75E+08 0. 2.03E+08 NI-63 7.04E+08 4.88E+07 0. 0. 0. 1.02E+07 0. 2.36E+07 ZN-65 1.33E+08 4.22E+08 0. 2.82E+08 0. 2.66E+08 0. 1.91 E+08 RB-86 0. 1.82E+08 0. 0. 0. 3.59E+07 0. 8.50E+07 SR-89 5.04E+08 0. 0. 0. 0. 1.88E+07 0. 1.44E+07 SR-90 1.05E+10 0. 0. 0. 0. 7.02E+08 0. 2.67E+09 Y-91 1.76E+06 0. 0. 0. 0. 2.33E+08 0. 4.69E+04 ZR-95 4.62E+06 1.51 E+06 0. 7.47E+05 0. 2.22E+09 0. 1.20E+06 NB-95 2.68E+06 1.15E+06 0. 4.72E+05 0. 1.98E+09 0. 8.41E+05 RU-103 1.54E+08 0. 0. 1.51E+08 0. 3.81E+09 0. 5.87E+07 RU-106 4.51E+09 0. 0. 2.02E+09 0. 7.01E+10 0. 5.61E+08 AG-11iM 2.50E+06 2.31E+06 0. 4.55E+06 0. 9.44E+08 0. 1.38E+06 CD-115M 0. 5.45E+05 0. 4.32E+05 0. 2.29E+07 0. 1.74E+04 NOTE - T BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, XdlQ, AND D/Q.

THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B - 22 11/22/02

TURKEY POINT UNIT 3 & 4 0FFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVEE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-COW-MEAT (CONTAMINATED FORAGE) AGE GROUP - CHILD NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 0. 0. 0. 0. 0. 0. 0. 0.

SN-126 6.92E+09 1.37E+08 4.02E+07 0. 2.41E+06 2.31E+09 0. 1.98E+08 SB-124 7.40E+06 1.40E+05 1.79E+04 0. 5.74E+06 2.1OE+08 0. 2.93E+06 SB-125 7.66E+07 1.84E+07 1.90E+07 6.47E+07 9.26E+08 1.44E+08 0. 1.08E+07 TE-125M 5.69E+08 1.54E+08 1.60E+08 5.44E+08 0. 5.49E+08 0. 7.59E+07 TE-127M 4.40E+08 1.51 E+08 1.24E+08 1.70E+09 0. 2.54E+09 0. 5.61E+07 TE-129M 1.84E+09 5.12E+08 5.87E+08 1.78E+09 0. 2.21E+09 0. 2.84E+08 1-130 8.87E-07 2.63E-06 3.34E-04 4.08E-06 0. 2.25E-06 0. 1.03E-06 1-131 1.58E+07 1.62E+07 5.25E+09 9.86E+06 0. 1.38E+06 0. 1.22E+07 1-132 0. 0. 0. 0. 0. 0. 0. 0.

1-133 6.86E-01 8.47E-01 2.04E+02 4.97E-01 0. 3.43E-01 0. 3.33E-01 1-134 0. 0. 0. 0. 0. 0. 0. 0.

1-135 3.21E-02 2.96E-02 0. 1.12E-02 3.37E-03 6.92E-04 0. 1.32E-02 CS-1 34 8.83E+08 1.49E+09 0. 1.89E+08 1.65E+08 8.04E+06 0. 3.16E+08 CS-136 4.41E+06 1.74E+07 0. 9.69E+06 1.33E+06 1.98E+06 0. 1.25E+07 CS-137 1.27E+09 1.23E+09 0. 1.51E+08 1.44E+08 7.50E+06 0. 1.84E+08 BA-1 40 4.37E+07 3.84E+04 0. 4.59E+03 2.29E+04 6.03E+06 0. 2.57E+06 CE-141 2.1OE+04 1.05E+04 0. 1.65E+03 0. 1.32E+07 0. 1.57E+03 CE-144 2.38E+06 7.46E+05 0. 1.35E+05 0. 1.94E+08 0. 1.27E+05 PR-143 7.96E+03 3.20E+03 0. 1.84E+03 0. 3.48E+07 0. 3.95E+02 ND-147 6.40E+03 3.47E+03 0. 2.48E+03 0. 1.53E+07 0. 3.27E+02 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR x/Q. X,JQ. AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B-23 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-COWS-MILK (CONTAMINATED FORAGE) AGE GROUP - ADULT NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 9.73E+02 9.73E+02 9.73E+02 9.73E+02 9.73E+02 0. 9.73E+02 C-14 3.63E+05 7.28E+04 7.28E+04 7.28E+04 7.28E+04 7.28E+04 0. 7.28E+04 P-32 1.71E+10 1.07E+09 0. 0. 0. 1.92E+09 0. 6.62E+08 CR-51 0. 0. 1.71 E+04 6.32E+03 3.80E+04 7.20E+06 0. 2.86E+04 MN-54 0. 8.41E+06 0. 2.50E+06 0. 2.58E+07 0. 1.61E+06 FE-59 2.98E+07 7.06E+07 0. 0., 1.96E+07 2.33E+08 0. 2.69E+07 CO-57 0. 1.28E+06 0. 0. 0. 3.25E+07 0. 2.13E+06 CO-58 0. 4.72E+06 0. 0. 0. 9.56E+07 0. 1.06E+07 CO-60 0. 1.65E+07 0. 0. 0. 3.08E+08 0. 3.62E+07 NI-63 6.73E+09 4.67E+08 0. 0. 0. 9.73E+07 0. 2.26E+08 ZN-65 1.37E+09 4.36E+09 0. 2.92E+09 0. 2.75E+09 0. 1.98E+09 RB-86 0. 2.60E+09 0. 0.. 0. 5.12E+08 0. 1.21E+09 SR-89 1.46E+09 0. 0. 0. 0. 2.33E+08 0. 4.17E+07 SR-90 4.70E+10 0. 0. 0.. 0. 6.37E+08 0. 1.15E+10 Y-91 8.60E+03 0. 0. 0. 0. 4.73E+06 0. 2.31E+02 ZR-95 3.18E+04 1.75E+04 0. 1.75E+04 0. 1.05E+08 0. 6.95E+03 NB-95 8.26E+04 4.59E+04 0. 4.55E+04 0. 2.79E+08 0. 1.80E+04 RU-103 1.02E+03 0. 0. 3.91E+03 0. 1.19E+05 0. 4.41E+02 RU-106 2.04E+04 0. 0. 3.95E+04 0. 1.32E+06 0. 2.58E+03 AG-110M 5.84E+07 5.40E+07 0. 1.96E+08 0. 2.20E+10 0. 3.21E+07 CD-115M 0. 1.25E+06 0. 9.89E+05 0. 5.24E+07 0. 3.98E+04 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q,O xdQ, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B- 24 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3,0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-COWS-MILK (CONTAMINATED FORAGE) AGE GROUP - ADULT NUCLIDE ORGAN DOSE FACTOR (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 0. 0. 0. 0. 0. 0. 0. 0.

SN-126 1.65E+09 3.27E+07 9.56E+06 0. 4.67E+06 1.09E+09 0. 4.94E+07 SB-124 2.58E+07 4.87E+05 6.24E+04 0. 2.OOE+07 7.31E+08 0. 1.02E+07 SB-125 2.84E+07 6.06E+05 2.99E+05 3.72E+06 2.66E+09 2.29E+08 0. 5.23E+06 TE-125M 1.63E+07 5.91E+06 4.91E+06 6.63E+07 0. 6.50E+07 0. 2.18E+06 TE-127M 4.63E+07 1.63E+07 1.21E+07 1.88E+08 0. 2.11E+08 0. 5.72E+06 TE-129M 8.06E+07 2.27E+07 2.09E+07 2.53E+08 0. 3.04E+08 0. 9.61 E+06 1-130 4.27E+05 1.26E+08 1.61 E+08 1.96E+06 0. 1.08E+06 0. 4.97E+05 1-131 2.96E+08 4.25E+08 1.39E+11 7.27E+08 0. 1.12E+08 0. 2.43E+08 1-132 1.67E-01 4.47E-01 5.88E+01 7.12E-01 0. 8.39E-02 0. 1.59E-01 1-133 4.00E+06 6.94E+06 1.33E+09 1.21E+07 0. 6.10E+06 0. 2.12E+06 1-134 0. 0. 9.98E-10 0. 0. 0. 0. 0.

1-135 1.40E+04 3.70E+04 4.84E+06 5.88E+04 7.58E-02 4.14E+04 0. 1.36E+04 CS-134 5.66E+09 1.35E+10 0. 4.36E+09 1.45E+09 2.36E+08 0. 1.10E+10 CS-136 2.61E+08 1.03E+09 0. 5.74E+08 7.87E+07 1.17E+08 0. 7.43E+08 CS-137 7.39E+09 1.01E+10 0. 3.44E+09 1.14E+09 1.95E+08 0. 6.62E+09 BA-140 2.69E+07 3.38E+04 0. 1.15E+04 1.93E+04 5.70E+07 0. 1.78E+06 CE-141 2.91E+04 1.97E+04 0. 9.13E+03 0. 7.52E+07 0. 2.23E+03 CE-144 2.15E+06 8.97E+05 0. 5.32E+05 0. 7.26E+08 0. 1.15E+05 PR-143 1.59E+02 6.39E+01 0. 3.68E+01 0. 6.96E+05 0. 7.89E+00 ND-147 1.16E+02 1.12E+02 0. 6.77E+01 0. 5.28E+05 0. 7.34E+00 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, XyIQ, AND D/Q.

NOTE -THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B - 25 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-COWS-MILK (CONTAMINATED FORAGE) AGE GROUP - TEENAGER NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 9.93E+02 9.93E+02 1.26E+03 9.93E+02 9.93E+02 0. 9.93E+02 C-14 1.25E+05 1.25E+05 1.25E+05 9.39E+04 1.25E+05 1.25E+05 0. 1.25E+05 P-32 2.21E+10 1.38E+09 0. 0. 0. 2.48E+09 0. 8.54E+08 CR-51 0. 0. 2.21 E+04 8.15E+03 4.90E+04 9.29E+06 0. 3.69E+04 MN-54 0. 1.09E+07 0. 3.32E+06 0. 3.33E+07 0. 2.07E+06 FE-59 3.84E+07 9.12E+07 0. 0. 2.53E+07 3.01E+08 0. 3.47E+07 CO-57 0. 1.65E+06 0. 0. 0. 4.19E+07 0. 2.75E+06 CO-58 0. 8.1OE+06 0. 0. 0. 1.1OE+08 0. 1.85E+07 CO-60 0. 2.73E+07 0. 0. 0. 3.27E+08 0. 6.23E+07 NI-63 8.68E+09 6.02E+08 0. 0. 0. 1.26E+08 0. 2.91E+08 ZN-65 1.77E+09 5.63E+09 0. 3.77E+09 0. 3.55E+09 0. 2.55E+09 RB-86 0. 3.35E+09 0. 0. 0. 6.61 E+08 0. 1.56E+09 SR-89 2.80E+09 0. 0. 0. 0. 3.03E+08 0. 8.03E+07 SR-90 8.29E+10 0. 0. 0. 3.38E+06 1.76E+09 0. 2.05E+10 Y-91 1.54E+04 0. 0. 0. 0. 5.93E+06 0. 4.12E+02 ZR-95 4.78E+04 2.84E+04 0. 2.25E+04 0. 1.15E+08 0. 1.60E+04 NB-95 1.24E+05 7.46E+04 0. 5.87E+04 0. 3.05E+08 0. 4.21E+04 RU-103 1.69E+03 0. 0. 5.04E+03 0. 1.32E+05 0. 7.56E+02 RU-106 3.83E+04 0. 0. 5.09E+04 0. 1.73E+06 0. 4.81E+03 AG-A11M 7.53E+07 6.97E+07 0. 1.37E+08 0. 2.84E+10 0. 4.14E+07 CD-115M 0. 1.61E+06 0. 1.28E+06 0. 6.77E+07 0. 5.14E+04 BASED ON I p.Ci/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, XdJQ, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B- 26 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-COWS-MILK (CONTAMINATED FORAGE) AGE GROUP - TEENAGER NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 0. 0. 0. 0. 0. 0. 0. 0.

SN-126 2.12E+09 4.21E+07 1.24E+07 0. 6.03E+06 1.41E+09 0. 6.37E+07 SB-124 3.33E+07 6.29E+05 8.05E+04 0. 2.59E+07 9.43E+08 0. 1.32E+07 SB-1 25 3.45E+07 9.58E+05 5.05E+05 4.80E+06 3.43E+09 2.95E+08 0. 6.82E+06 TE-125M 3.OOE+07 1.08E+07 8.47E+06 8.55E+07 0. 8.39E+07 0. 3.98E+06 TE-127M 6.02E+07 2.11E+07 1.59E+07 2.43E+08 0. 3.02E+08 0. 7.45E+06 TE-129M 1.13E+08 4.18E+07 3.61E+07 3.27E+08 0. 3.93E+08 0. 1.78E+07 1-130 5.51E+05 1.63E+06 2.07E+08 2.53E+06 0. 1.40E+06 0. 6.41E+05 1-131 5.12E+08 7.24E+08 2.09E+11 9.38E+08 0. 1.37E+08 0. 4.31E+08 1-132 2.16E-01 5.76E-01 7.59E+01 9.19E-01 0. 1.08E-01 0. 2.05E-01 1-133 7.33E+06 1.24E+07 2.26E+09 1.56E+07 0. 9.02E+06 0. 3.83E+06 1-134 0. 0. 1.29E-09 0.' 0. 0. 0. 0.

1-135 1.81 E+04 4.77E+04 6.24E+06 7.58E+04 9.79E-02 5.34E+04 0. 1.75E+04 CS-1 34 9.44E+09 2.28E+10 0. 5.63E+09 2.76E+09 2.63E+08 0. 1.06E+10 CS-136 3.37E+08 1.33E+09 0. 7.41E+08 1.02E+08 1.51E+08 0. 9.58E+08 CS-137 1.28E+10 1.72E+10 0. 4.43E+09 2.28E+09 2.29E+08 0. 6.04E+09 BA-140 4.84E+07 5.95E+04 0. 1.48E+04 3.98E+04 9.16E+06 0. 3.11E+06 CE-141 5.05E+04 3.39E+04 0. 1.18E+04 0. 9.18E+07 0. 3.89E+03 CE-144 4.1OE+06 1.68E+06 0. 6.87E+05 0. 9.65E+08 0. 2.17E+05 PR-143 2.05E+02 8.25E+01 0. 4.75E+01 0. 8.98E+05 0. 1.02E+01 ND-147 1.49E+02 1.44E+02 0. 8.74E+01 0. 6.82E+05 0. 9.48E+00 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FORIXQ, Xd/Q, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER)

,3B1- 27.

11/22/02

,. i

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-COWS-MILK (CONTAMINATED FORAGE) AGE GROUP - CHILD NUCLIDE ORGAN DOSE FACTOR (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 1.57E+03 1.57E+03 1.04E+03 1.57E+03 1.57E+03 0. 1.57E+03 C-14 3.08E+05 3.08E+05 3.08E+05 7.75E+04 3.08E+05 3.08E+05 0. 3.08E+05 P-32 1.82E+10 1.14E+09 0. 0. 0. 2.05E+09 0. 7.05E+08 CR-51 0. 0. 1.82E+04 6.72E+03 4.04E+04 7.66E+06 0. 3.05E+04 MN-54 0. 8.96E+06 0. 2.67E+06 0. 2.74E+07 0. 1.71E+06 FE-59 3.17E+07 7.52E+07 0. 0. 2.09E+07 2.48E+08 0. 2.86E+07 CO-57 0. 1.36E+06 0. 0. 0. 3.46E+07 0. 2.27E+06 CO-58 0. 1.25E+07 0. 0. 0. 7.41 E+07 0. 3.76E+07 CO-60 0. 4.22E+07 0. 0. 0. 2.33E+08 0. 1.27E+08 NI-63 7.16E+09 4.97E+08 0. 0. 0. 1.04E+08 0. 2.40E+08 ZN-65 1.46E+09 4.65E+09 0. 3.11E+09 0. 2.93E+09 0. 2.10E+09 RB-86 0. 2.77E+09 0. 0. 0. 5.45E+08 0. 1.29E+09 SR-89 6.92E+09 0. 0. 0. 0. 2.58E+08 0. 1.98E+08 SR-90 1.13E+11 0. 0. 0. 0. 1.52E+09 0. 2.87E+10 Y-91 3.80E+04 0. 0. 0. 0. 5.05E+06 0. 1.01E+03 ZR-95 1.06E+05 4.47E+04 0. 1.86E+04 0. 7.68E+07 0. 3.29E+04 NB-95 2.75E+05 1.18E+05 0. 4.84E+04 0. 2.03E+08 0. 8.63E+04 RU-103 3.99E+03 0. 0. 4.16E+03 0. 1.05E+05 0. 1.61E+03 RU-106 9.39E+04 0. 0. 4.20E+04 0. 1.46E+06 0. 1.17E+04 AG-110M 6.21E+07 5.75E+07 0. 1.13E+08 0. 2.35E+10 0. 3.42E+07 CD-115M 0. 1.33E+06 0. 1.05E+06 0. 5.58E+07 0. 4.24E+04 BASED ON 1 .Ci/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, XSQ, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B - 28 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-COWS-MILK (CONTAMINATED FORAGE) AGE GROUP - CHILD NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 0. 0. 0. 0. 0. 0. 0. 0.

SN-126 1.75E+09 3.48E+07 1.01E+07 0. 4.97E+06 1.16E+09 0. 5.25E+07 SB-124 2.75E+07 5.19E+05 6.64E+04 0. 2.13E+07 7.78E+08 0. 1.09E+07 SB-125 3.13E+07 1.41E+05 1.18E+06 3.96E+06 2.83E+09 2.43E+08 0. 5.99E+06 TE-125M 7.38E+07 2.OOE+07 2.07E+07 7.05E+07 0. 7.12E+07 0. 9.84E+06 TE-127M 5.18E+07 1.78E+07 1.46E+07 2.OOE+08 0. 2.99E+08 0. 6.60E+06 TE-129M 2.77E+08 7.73E+07 8.85E+07 2.70E+08 0. 3.33E+08 0. 4.28E+07 1-130 4.54E+05 1.35E+06 1.71E+08 2.09E+06 0. 1.15E+06 0. 5.29E+05 1-131 1.24E+09 1.27E+09 4.12E+11 7.74E+08 0. 1.09E+08 0. 9.56E+08 1-132 1.18E-01 4.76E-01 6.26E+01 7.58E-01 0. 8.93E-02 0. 1.69E-01 1-133 1.78E+07 2.20E+07 5.30E+09 1.29E+07 0. 8.90E+06 0. 8.63E+06 1-134 0. 0. 1.06E-09 0. 0. 0. 0. 0.

1-135 1.49E+04 3.94E+04 5.15E+06 6.26E+04 8.07E-02 4.41 E+04 0. 1.44E+04 CS-134 2.17E+10 3.65E+10 0. 4.65E+09 4.06E+09 1.97E+08 0. 7.76E+09 CS-136 2.78E+08 1.10E+09 0. 6.11E+08 8.37E+07 1.25E+08 0. 7.90E+08 CS-137 3.08E+10 2.98E+10 0. 3.66E+09 3.49E+09 1.81E+08 0. 4.44E+09 BA-140 1.17E+08 1.02E+05 0. 1.22E+04 6.09E+04 7.75E+06 0. 6.84E+06 CE-141 1.24E+05 6.22E+04 0. 9.72E+03 0. 7.80E+07 0. 9.26E+03 CE-144 1.00E+07 3.14E+06 0. 5.67E+05 0. 8.15E+08 0. 5.34E+05 PR-143 1.69E+02 6.80E+01 0. 3.92E+01 0. 7.41 E+05 0. 8.40E+00 ND-147 1.23E+02 1.19E+02 0. 7.21E+01 0. 5.63E+05 0. 7.81E+00 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR x/Q, XdlQ, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B - 29 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-COWS-MILK (CONTAMINATED FORAGE) AGE GROUP - INFANT NUCLIDE . ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 2.37E+03 2.37E+03 1.04E+03 2.37E+03 2.37E+03 0. 2.37E+03 C-14 6.55E+05 6.55E+05 6.55E+05 7.55E+04 6.55E+05 6.55E+05 0. 6.55E+05 P-32 1.82E+10 1.14E+09 0. 0. 0. 2.05E+09 0. 7.05E+08 CR-51 0. 0. 1.82E+04 6.72E+03 4.04E+04 7.66E+06 0. 3.05E+04 MN-54 0. 8.96E+06 0. 2.67E+06 0. 2.74E+07 0. 1.71 E+06 FE-59 3.17E+07 7.52E+07 0. 0. 2.09E+07 2.48E+08 0. 2.86E+07 CO-57 0. 1.36E+06 0. 0. 0. 3.46E+07 0. 2.27E+06 CO-58 0. 2.55E+07 0. 0. 0. 6.60E+07 0. 6.24E+07 CO-60 0. 8.73E+07 0. 0. 0. 2.16E+08 0. 2.09E+08 NI-63 7.16E+09 4.97E+08 0. 0. 0. 1.04E+08 0. 2.40E+08 ZN-65 1.46E+09 4.65E+09 0. 3.11E+09 0. 2.93E+09 0. 2.1OE+09 RB-86 0. 2.77E+09 0. 0. 0. 5.45E+08 0. 1.29E+09 SR-89 1.47E+10 0. 0. 0. 0. 2.75E+08 0. 4.22E+08 SR-90 1.65E+11 0. 0. 0. 0. 1.61E+09 0. 4.21E+10 Y-91 8.12E+04 0. 0. 0. 0. 5.37E+06 0. 2.16E+03 ZR-95 2.12E+05 9.41 E+04 0. 1.86E+04 0. 7.47E+07 0. 5.56E+04 NB-95 5.49E+05 2.47E+05 0. 4.84E+04 0. 1.98E+08 0. 1.45E+05 RU-103 8.30E+03 0. 0. 4.16E+03 0. 1.04E+05 0. 2.86E+03 RU-106 2.01E+05 0. 0. 4.20E+04 0. 1.56E+06 0. 2.46E+04 AG-110M 6.21E+07 5.75E+07 0. 1.13E+08 0. 2.35E+10 0. 3.42E+07 CD-115M 0. 1.33E+06 0. 1.05E+06 0. 5.58E+07 0. 4.24E+04 BASED ON 1 p.Ci/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, IJQ, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER)

S3B - 30 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-COWS-MILK (CONTAMINATED FORAGE) AGE GROUP - INFANT NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 0. 0. 0. 0. 0. 0. 0. 0.

SN-126 1.75E+09 3.48E+07 1.01E+07 0. 4.97E+06 1.16E+09 0. 5.25E+07 SB-124 2.75E+07 5.19E+05 6.64E+04 0. 2.13E+07 7.78E+08 0. 1.09E+07 SB-125 3.59E+07 3.17E+06 2.93E+06 3.96E+06 2.83E+09 2.43E+08 0. 6.62E+06 TE-125M 1.57E+08 5.30E+07 5.18E+07 7.05E+07 0. 7.57E+07 0. 2.1OE+07 TE-127M 5.54E+07 1.93E+07 1.79E+07 2.OOE+08 0. 3.24E+08 0. 7.38E+06 TE-129M 5.87E+08 2.02E+08 2.21 E+08 2.70E+08 0. 3.54E+08 0. 8.95E+07 1-130 4.54E+05 1.35E+06 1.71 E+08 2.09E+06 0. 1.15E+06 0. 5.29E+05 1-131 2.59E+09 3.09E+09 9.94E+11 7.74E+08 0. 1.16E+08 0. 1.81 E+09 1-132 1.78E-01 4.76E-01 6.26E+01 7.58E-01 0. 8.93E-02 0. 1.69E-01 1-133 3.75E+07 5.48E+07 1.30E+10 1.29E+07 0. 9.74E+06 0. 1.66E+07 1-134 0. 0. 1.06E-09 0. 0. 0. 0. 0.

1-135 1.49E+04 3.94E+04 5.15E+06 6.26E+04 8.07E-02 4.41 E+04 0. 1.44E+04 CS-134 4.48E+10 7.97E+10 0. 4.65E+09 9.12E+09 1.90E+08 0. 6.75E+09 CS-1 36 2.78E+08 1.10E+09 0. 6.11E+08 8.37E+07 1.25E+08 0. 7.90E+08 CS-137 6.44E+10 7.21E+10 0. 3.66E+09 8.69E+09 1.86E+08 0. 4.14E+09 BA-140 2.45E+08 2.47E+05 0. 1.22E+04 1.51E+05 8.13E+06 0. 1.27E+07 CE-141 2.65E+05 1.62E+05 0. 9.72E+03 0. 7.87E+07 0. 1.90E+04 CE-144 2.1OE+07 8.29E+06 0. 5.67E+05 0. 8.66E+08 0. 1.13E+06 PR-143 1.69E+02 6.80E+01 0. 3.92E+01 0. 7.41 E+05 0. 8.40E+00 ND-147 1.23E+02 1.19E+02 0. 7.21E+01 0. 5.63E+05 0. 7.81E+00 BASED ON 1 piCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR x/Q, XJQ, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREMNR PER UCI/CU.METER) 3B-31 11/22/02

I Ii TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-GOATS-MILK (CONTAMINATED FORAGE) AGE GROUP - ADULT NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 1.99E+03 1.99E+03 1.99E+03 1.99E+03 1.99E+03 0. 1.99E+03 C-14 3.63E+05 7.28E+04 7.28E+04 7.28E+04 7.28E+04 7.28E+04 0. 7.28E+04 P-32 2.05E+10 1.29E+09 0. 0. 0. 2.31E+09 0. 7.94E+08 CR-51 0. 0. 2.05E+08 7.58E+02 4.56E+03 8.64E+05 0. 3.43E+03 MN-54 0. 1.01 E+06 0. 3.00E+05 0. 3.09E+06 0. 1.93E+05 FE-59 3.87E+05 9.18E+05 0. 0. 2.55E+05 3.03E+06 0. 3.50E+05 CO-57 0. 1.54E+05 0. 0. 0. 3.90E+06 0. 2.55E+05 CO-58 0. 5.67E+05 0. 0. 0. 1.15E+07 0. 1.27E+06 CO-60 0. 1.98E+06 0. 0. 0. 3.70E+07 0. 4.34E+06 NI-63 8.07E+08 5.60E+07 0. 0. 0. 1.17E+07 0. 2.71E+07 ZN-65 1.65E+08 5.24E+08 0. 3.50E+08 0. 3.30E+08 0. 2.37E+08 RB-86 0. 3.12E+08 0. 0. 0. 6.15E+07 0. 1.45E+08 SR-89 3.06E+09 0. 0. 0. 0. 4.89E+08 0. 8.76E+07 SR-90 9.87E+10 0. 0. 0. 0. 1.32E+09 0. 2.41E+10 Y-91 1.03E+03 0. 0. 0. 0. 5.68E+05 0. 2.77E+01 ZR-95 3.82E+03 2.1OE+03 0. 2.1OE+03 0. 1.26E+07 0. 8.34E+02 NB-95 9.92E+03 5.51E+03 0. 5.46E+03 0. 3.34E+07 0. 2.173+03 RU-103 1.23E+02 0. .0. 4.69E+02 0. 1.43E+04 0. 5.30E+01 RU-106 2.45E+03 0. 0. 4.73E+03 0. 1.58E+05 0. 3.1OE+02 AG-i 10M 7.OOE+06 6.48E+06 0. 1.27E+07 0. 2.64E+09 0. 3.85E+06 CD-115M 0. 1.50E+05 0. 1.19E+05 0. 6.29E+06 0. 4.78E+03 BASED ON 1 ýtCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, XJQ, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREMNR PER UCI/CU.METER) 3B - 32 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-GOATS-MILK (CONTAMINATED FORAGE) AGE GROUP - ADULT NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 0. 0. 0. 0. 0. 0. 0. 0.

SN-126 1.97E+08 3.92E+06 1.15E+06 0. 5.61E+05 1.31 E+08 0. 5.92E+06 SB-124 3.1OE+06 5.85E+04 7.49E+03 0. 2.40E+06 8.77E+07 0. 1.22E+06 SB-125 3.16E+06 7.28E+04 3.58E+04 4.47E+05 3.19E+08 2.74E+07 0. 6.29E+05 TE-125M 1.96E+06 7.1OE+05 5.89E+05 7.95E+06 0. 7.81E+06 0. 2.62E+05 TE-127M 5.57E+06 1.94E+06 1.47E+06 2.26E+07 0. 2.52E+07 0. 6.86E+05 TE-129M 7.27E+06 2.72E+06 2.51E+06 3.04E+07 0. 3.65E+07 0. 1.15E+06 1-130 5.12E+05 1.52E+06 1.93E+08 2.36E+06 0. 1.30E+06 0. 5.96E+05 1-131 3.56E+08 5.1OE+08 1.67E+11 8.72E+08 0. 1.34E+08 0. 2.92E+08 1-132 2.00E-01 5.36E-01 7.06E+01 8.55E-01 0. 1.01 E-01 0. 1.91 E-01 1-133 4.80E+06 8.32E+06 1.60E+09 1.45E+07 0. 7.32E+06 0. 2.54E+06 1-134 0. 0. 1.20E-09 0. 0. 0. 0. 0.

1-135 1.68E+04 4.44E+04 5.80E+06 7.05E+04 2.28E-01 4.97E+04 0. 1.63E+04 CS-134 1.78E+10 4.04E+10 0. 1.31E+10 4.34E+09 7.06E+08 0. 3.30E+10 CS-136 7.84E+08 3.09E+09 0. 1.72E+09 2.36E+08 3.52E+08 0. 2.23E+09 CS-137 2.22E+10 3.03E+10 0. 1.03E+10 3.42E+09 5.83E+08 0. 1.99E+10 BA-140 3.23E+06 4.05E+03 0. 1.38E+03 2.32E+03 6.84E+06 0. 2.13E+05 CE-141 3.49E+03 2.36E+03 0. 1.10E+03 0. 9.02E+06 0. 2.68E+02 CE-144 2.58E+05 1.08E+05 0. 6.39E+04 0. 8.71E+07 0. 1.38E+04 PR-143 1.91E+01 7.67E+00 0. 4.42E+00 0. 8.35E+04 0. 9.47E-01 ND-147 1.39E+01 1.34E+01 0. 8.13E+00 0. 6.35E+04 0. 8.81E-01 BASED ON 1 p.Ci/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, XJQ, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B - 33 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-GOATS-MILK (CONTAMINATED FORAGE) AGE GROUP - TEENAGER NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 2.03E+03 2.03E+03 2.56E+03 2.03E+03 2.03E+03 0. 2.03E+03 C-14 1.25E+05 1.25E+05 1.25E+05 9.39E+04 1.25E+05 1.25E+05 0. 1.25E+05 P-32 2.65E+10 1.66E+09 0. 0. 0. 2.98E+09 0. 1.03E+09 CR-51 0. 0. 2.65E+03 9.78E+02 5.88E+03 1.11E+06 0. 4.43E+03 MN-54 0. 1.30E+06 0. 3.88E+05 0. 3.99E+06 0. 2.49E+05 FE-59 4.99E+05 1.19E+06 0. 0." 3.29E+05 3.91E+06 0. 4.51E+05 CO-57 0. 1.98E+05 0. 0.. 0. 5.03E+06 0. 3.30E+05 CO-58 0. 9.72E+05 0. 0.. 0. 1.31 E+07 0. 2.22E+06 CO-60 0. 3.28E+06 0. 0.' 0. 3.93E+07 0. 7.48E+06 NI-63 1.04E+09 7.23E+07 0. 0. 0. 1.51 E+07 0. 3.49E+07 ZN-65 2.13E+08 6.76E+08 0. 4.52E+08 0. 4.26E+08 0. 3.06E+08 RB-86 0. 4.02E+08 0. 0. 0. 7.93E+07 0. 1.88E+08 SR-89 5.87E+09 0. 0. 0. 0. 6.37E+08 0. 1.69E+08 SR-90 1.74E+11 0. 0. 0." 4.05E+05 3.68E+09 0. 4.30E+10 Y-91 1.85E+03 0. 0. 0. . 0. 7.11E+05 0. 4.94E+01 ZR-95 5.74E+03 3.41E+03 0. 2:70E+03 0. 1.38E+07 0. 1.93E+03 NB-95 1.49E+04 8.96E+03 0. 7,.05E+03 0. 3.66E+07 0. 5.05E+03 RU-103 2.03E+02 0. 0. 6.05E+02 0. 1.58E+04 0. 9.08E+01 RU-1 06 4.59E+03 0. 0. 6.11E+03 0. 2.08E+05 0. 5.78E+02 AG-110M 9.04E+06 8.36E+06 0. 1.64E+07 0. 3.41E+09 0. 4.97E+06 CD-115M 0. 1.93E+05 0. 1.53E+05 0. 8.12E+06 0. 6.17E+03 BASED ON 1 ýtCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, xJQ, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B - 34 11/22/02

TURKEY POINT UNIT 3 & 4 0FFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GA\SEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-GOATS-MILK (CONTAMINATED FORAGE) AGE GROUP - TEENAGER NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID IKIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 0. 0. 0. 0. 0. 0. 0. 0.

SN-126 2.54E+08 5.05E+06 1.48E+06 0. 7.23E+05 1.69E+08 0. 7.64E+06 SB-124 4.00E+06 7.54E+04 9.66E+03 0. 3.1OE+06 1.13E+08 0. 1.58E+06 SB-125 4.14E+06 1.15E+05 6.06E+04 5.77E+05 4.12E+08 3.54E+07 0. 8.19E+05 TE-125M 3.61E+06 1.29E+06 1.02E+06 1.03E+07 0. 1.01E+07 0. 4.78E+05 TE-127M 7.23E+06 2.52E+06 1.91 E+06 2.92E+07 0. 3.63E+07 0. 8.94E+05 TE-129M 1.35E+07 5.02E+06 4.34E+06 3.92E+07 0. 4.72E+07 0. 2.13E+06 1-130 6.61 E+05 1.96E+06 2.49E+08 3.04E+06 0. 1.68E+06 0. 7.69E+05 1-131 6.15E+08 8.68E+08 2.50E+11 1.13E+09 0. 1.64E+08 0. 5.17E+08 1-132 2.59E-01 6.92E-01 9.11E+01 1.10E+00 0. 1.30E-01 0. 2.46E-01 1-133 8.79E+06 1.49E+07 2.71 E+09 1.88E+07 0. 1.08E+07 0. 4.59E+06 1-134 0. 0. 1.55E-09 0. 0. 0. 0. 0.

1-135 2.17E+04 5.73E+04 7.49E+06 9.1OE+04 2.94E-01 6.41E+04 0. 2.1OE+04 CS-134 2.88E+10 6.83E+10 0. 1.69E+10 8.27E+09 7.88E+08 0. 3.19E+10 CS-1 36 1.01E+09 3.99E+09 0. 2.22E+09 3.05E+08 4.54E+08 0. 2.87E+09 CS-137 3.84E+10 5.16E+10 0. 1.33E+10 6.85E+09 6.88E+08 0. 1.81E+10 BA-140 5.81E+06 7.14E+03 0. 1.78E+03 4.78E+03 1.10E+06 0. 3.73E+05 CE-141 6.06E+03 4.07E+03 0. 1.41E+03 0. 1.10E+07 0. 4.66E+02 CE-144 4.92E+05 2.02E+05 0. 8.24E+04 0. 1.16E+08 0. 2.61E+04 PR-143 2.46E+01 9.90E+00 0. 5.70E+00 0. 1.08E+05 0. 1.22E+00 ND-147 1.79E+01 1.73E+01 0. 1.05E+01 0. 8.19E+04 0. 1.14E+00 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR ;/Q, XJQ, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B - 35 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-GOATS-MILK (CONTAMINATED FORAGE) AGE GROUP - CHILD NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 3.20E+03 3.20E+03 2.11E+03 3.20E+03 3.20E+03 0. 3.20E+03 C-14 3.08E+05 3.08E+05 3.08E+05 7.75E+04 3.08E+05 3.08E+05 0. 3.08E+05 P-32 2.19E+10 1.37E+09 0. 0., 0. 2.46E+09 0. 8.46E+08 CR-51 0. 0. 2.19E+03 8.07E+02 4.85E+03 9.19E+05 0. 3.66E+03 MN-54 0. 1.08E+06 0. 3.20E+05 0. 3.29E+06 0. 2.05E+05 FE-59 4.12E+05 9.78E+05 0. 0. 2.72E+05 3.23E+06 0. 3.72E+05 CO-57 0. 1.64E+05 0. 0. 0. 4.15E+06 0. 2.72E+05 CO-58 0. 1.50E+05 0. 0. 0. 8.90E+06 0. 4.51E+06 CO-60 0. 5.06E+06 0. 0., 0. 2.80E+07 0. 1.52E+07 NI-63 8.60E+08 5.96E+07 0. 0. 0. 1.24E+07 0. 2.88E+07 ZN-65 1.76E+08 5.57E+08 0. 3.73E+08 0. 3.51E+08 0. 2.52E+08 RB-86 0. 3.32E+08 0. 0., 0. 6.54E+07 0. 1.55E+08 SR-89 1.45E+10 0. 0. 0.', 0. 5.43E+08 0. 4.16E+08 SR-90 2.37E+11 0. 0. 0., 0. 3.16E+09 0. 6.02E+10 Y-91 4.56E+03 0. 0. 0.. 0. 6.06E+05 0. 1.22E+02 ZR-95 1.27E+04 5.37E+03 0. 2.23E+03 0. 9.22E+06 0. 3.96E+03 NB-95 3.30E+04 1.41E+04 0. 5.81E+03 0. 2.44E+07 0. 1.04E+04 RU-103 4.79E+02 0. 0. 4.99E+02 0. 1.26E+04 0. 1.94E+02 RU-106 1.13E+04 0. 0. 5.04E+03 0. 1.75E+05 0. 1.40E+03 AG-1I0M 7.45E+06 6.90E+06 0. 1.36E+07 0. 2.81E+09 0. 4.1OE+06 CD-115M 0. 1.59E+05 0. 1.26E+05 0. 6.70E+06 0. 5.09E+03 BASED ON 1 IpCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR xdQ

,/Q AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER),.,!'

3B - 36 11/22/02 t;*.{

' ,I ',n",rr itl,

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-GOATS-MILK (CONTAMINATED FORAGE) AGE GROUP - CHILD NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 0. 0. 0. 0. 0. 0. 0. 0.

SN-126 2.10E+08 4.17E+06 1.22E+06 0. 5.97E+05 1.40E+08 0. 6.30E+06 SB-124 3.30E+06 6.22E+04 7.97E+03 0. 2.56E+06 9.33E+07 0. 1.30E+06 SB-125 3.75E+06 1.70E+05 1.43E+05 4.76E+05 3.40E+08 2.92E+07 0. 7.19E+05 TE-125M 8.85E+06 2.40E+06 2.49E+06 8.46E+06 0. 8.54E+06 0. 1.18E+06 TE-127M 6.21E+06 2.14E+06 1.75E+06 2.40E+07 0. 3.58E+07 0. 7.92E+05 TE-129M 3.32E+07 9.27E+06 1.06E+07 3.23E+07 0. 4.OOE+07 0. 5.15E+06 1-130 5.45E+05 1.61 E+06 2.05E+08 2.51E+06 0. 1.38E+06 0. 6.35E+05 1-131 1.48E+09 1.52E+09 4.94E+11 9.28E+08 0. 1.30E+08 0. 1.15E+09 1-132 2.18E-01 5.71E-01 7.51E+01 9.10E-01 0. 1.07E-01 0. 2.03E-01 1-133 2.14E+07 2.64E+07 6.36E+09 1.55E+07 0. 1.07E+07 0. 1.04E+07 1-134 0. 0. 1.27E-09 0. 0. 0. 0. 0.

1-135 1.79E+04 4.72E+04 6.18E+06 7.51E+04 2.42E-01 5.29E+04 0. 1.73E+04 CS-134 6.50E+10 1.10E+11 0. 1.39E+10 1.22E+10 5.92E+08 0. 2.33E+10 CS-1 36 8.34E+08 3.29E+09 0. 1.83E+09 2.51 E+08 3.74E+08 0. 2.37E+09 CS-137 9.28E+10 8.93E+10 0. 1.10E+10 1.05E+10 5.44E+08 0. 1.33E+10 BA-140 1.48E+07 1.23E+04 0. 1.48E+03 7.31 E+03 9.30E+05 0. 8.21 E+05 CE-141 1.49E+04 7.46E+03 0. 1.17E+03 0. 9.36E+06 0. 1.11E+03 CE-144 1.20E+06 3.76E+05 0. 6.80E+04 0. 9.78E+07 0. 6.41E+04 PR-143 2.03E+01 8.16E+00 0. 4.70E+00 0. 8.89E+04 0. 1.01E+00 ND-147 1.47E+01 1.42E+01 0. 8.66E+00 0. 6.75E+04 0. 9.38E-01 BASED ON 1 giCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR x/Q, xJQ, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B - 37 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3,0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-GOATS-MILK (CONTAMINATED FORAGE) AGE GROUP - INFANT NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 4.84E+03 4.84E+03 2.11E+03 4.84E+03 4.84E+03 0. 4.84E+03 C-14 6.55E+05 6.55E+05 6.55E+05 7.75E+04 6.55E+05 6.55E+05 0. 6.55E+05 P-32 2.19E+10 1.37E+09 0. 0. 0. 2.46E+09 0. 8.46E+08 CR-51 0. 0. 2.19E+03 8.07E+02 4.85E+03 9.19E+05 0. 3.66E+03 MN-54 0. 1.08E+06 0. 3.20E+05 0. 3.29E+06 0. 2.05E+05 FE-59 4.12E+05 9.78E+05 0. 0. 2.72E+05 3.23E+06 0. 3.72E+05 CO-57 0. 1.64E+05 0. 0. 0. 4.15E+06 0. 2.72E+05 CO-58 0. 3.06E+06 0. 0. 0. 7.92E+06 0. 7.49E+06 CO-60 0. 1.05E+07 0. 0. 0. 2.59E+07 0. 2.51E+07 NI-63 8.60E+08 5.96E+07 0. 0. 0. 1.24E+07 0. 2.88E+07 ZN-65 1.76E+08 5.57E+08 0. 3.73E+08 0. 3.51E+08 0. 2.52E+08 RB-86 0. 3.32E+08 0. 0. 0. 6.54E+07 0. 1.55E+08 SR-89 3.09E+10 0. 0. 0. 0. 5.77E+08 0. 8.87E+08 SR-90 3.46E+11 0. 0. 0. 0. 3.35E+09 0. 8.83E+10 Y-91 9.74E+03 0. 0. 0. 0. 6.45E+05 0. 2.60E+02 ZR-95 2.54E+04 1.13E+04 0. 2.23E+03 0. 8.95E+06 0. 6.67E+03 NB-95 6.59E+04 2.97E+04 0. 5.81E+03 0. 2.37E+07 0. 1.75E+04 RU-103 9.96E+02 0. 0. 4.99E+02 0. 1.24E+04 0. 3.43E+02 RU-106 2.41E+04 0. 0. 5.04E+03 0. 1.87E+05 0. 2.96E+03 AG-110M 7.45E+06 6.90E+06 0. 1.36E+07 0. 2.81E+09 0. 4.10E+06 CD-115M 0. 1.59E+05 0. 1.26E+05 0. 6.70E+06 0. 5.09E+03 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, xJQ, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B - 38 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - AIR-GRASS-GOATS-MILK (CONTAMINATED FORAGE) AGE GROUP - INFANT NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 0. 0. 0. 0. 0. 0. 0. 0.

SN-126 2.1OE+08 4.17E+06 1.22E+06 0. 5.97E+05 1.40E+08 0. 6.30E+06 SB-124 3.30E+06 6.22E+04 7.97E+03 0. 2.56E+06 9.33E+07 0. 1.30E+06 SB-125 4.31E+06 3.92E+05 3.52E+05 4.76E+05 3.40E+08 2.92E+07 0. 7.94E+05 TE-125M 1.89E+07 6.36E+06 6.21E+06 8.46E+06 0. 9.09E+06 0. 2.52E+06 TE-127M 6.64E+06 2.31E+06 2.15E+06 2.40E+07 0. 3.88E+07 0. 8.85E+05 TE-129M 7.05E+07 2.42E+07 2.66E+07 3.23E+07 0. 4.25E+07 0. 1.07E+07 1-130 5.45E+05 1.61E+06 2.05E+08 2.51E+06 0. 1.38E+06 0. 6.35E+05 1-131 3.11E+09 3.70E+09 1.19E+12 9.28E+08 0. 1.39E+08 0. 2.17E+09 1-132 2.13E-01 5.71E-01 7.51E+01 9.10E-01 0. 1.07E-01 0. 2.03E-01 1-133 4.50E+07 6.57E+07 1.55E+10 1.55E+07 0. 1.17E+07 0. 1.99E+07 1-134 0. 0. 1.27E-09 0. 0. 0. 0. 0.

1-135 1.79E+04 4.72E+04 6.18E+06 7.51E+04 2.42E-01 5.29E+04 0. 1.73E+04 CS-134 1.33E+11 2.39E+11 0. 1.39E+10 2.74E+10 5.69E+08 0. 2.02E+10 CS-136 8.34E+08 3.29E+09 0. 1.83E+09 2.51E+08 3.74E+08 0. 2.37E+09 CS-137 1.93E+11 2.16E+11 0. 1.10E+10 2.61E+10 5.59E+08 0. 1.24E+10 BA-140 2.95E+07 2.96E+04 0. 1.47E+03 1.81E+04 9.76E+05 0. 1.52E+06 CE-141 3.17E+04 1.95E+04 0. 1.17E+03 0. 9.44E+06 0. 2.28E+03 CE-144 2.52E+06 9.95E+05 0. 6.80E+04 0. 1.04E+08 0. 1.36E+05 PR-143 2.03E+01 8.16E+00 0. 4.70E+00 0. 8.89E+04 0. 1.01E+00 ND-147 1.47E+01 1.42E+01 0. 8.66E+00 0. 6.75E+04 0. 9.38E-01 BASED ON 1 piCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR XI/Q, XdQ, AND D/Q. -

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B - 39 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - FRESH AND STORED FRUITS AND VEGETABLES AGE GROUP - ADULT NUCLIDE ORGAN DOSE FACTOR (SQ.M ETER-MREM/YR PER UCI/SEC BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 2.86E+03 2.86E+03 2.86E+03 2.86E+03 2.86E+03 0. 2.86E+03 C-14 8.97E+05 1.80E+05 1.80E+05 1.80E+05 1.80E+05 1.80E+05 0. 1.80E+05 P-32 1.41 E+09 8.81 E+07 0. 0. 0. 1.58E+08 0. 5.44E+07 CR-51 0. 0. 2.78E+04 1.03E+04 6.19E+04 1.17E+07 0. 4.66E+04 MN-54 0. 3.13E+08 0. 9.31E+07 0. 9.58E+08 0. 5.97E+07 FE-59 1.27E+08 3.01E+08 0. 0. 8.37E+07 9.95E+08 0. 1.15E+08 CO-57 0. 1.17E+07 0. 0. 0. 2.97E+08 0. 1.95E+07 CO-58 0. 3.08E+07 0. 0. 0. 6.24E+08 0. 6.90E+07 CO-60 0. 1.68E+08 0. 0. 0. 3.14E+09 0. 3.68E+08 NI-63 1.04E+10 7.22E+08 0. 0. 0. 1.50E+08 0. 3.49E+08 ZN-65 3.18E+08 1.01E+09 0. 6.75E+08 0. 6.35E+08 0. 4.56E+08 RB-86 0. 2.20E+08 0. 0. 0. 4.34E+07 0. 1.03E+08 SR-89 1.OOE+10 0. 0. 0. 0. 1.60E+09 0. 2.86E+08 SR-90 6.07E+11 0. 0. 0. 0. 1.61E+10 0. 1.49E+11 Y-91 5.14E+06 0. 0. 0. 0. 2.83E+09 0. 1.38E+05 ZR-95 1.40E+06 5.02E+05 0. 7.21 E+05 0. 1.92E+09 0. 3.06E+05 NB-95 1.42E+05 7.90E+04 0. 7.83E+04 0. 4.79E+08 0. 3.10E+04 RU-103 4.84E+06 0. 0. 1.86E+07 0. 5.66E+08 0. 2.09E+06 RU-106 1.93E+08 0. 0. 3.72E+08 0. 1.25E+10 0. 2.43E+07 AG-A11M 1.06E+07 9.81E+06 0. 1.93E+07 0. 4.01E+09 0. 5.84E+06 CD-115M 0. 5.17E+07 0. 4.10E+07 0. 2.17E+09 0. 1.65E+06 BASED ON 1 [iCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, xdWQ, AND D/Q.

NOTE -THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B - 40 11/22/02

iýk TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - FRESH AND STORED FRUITS AND VEGETABLES AGE GROUP - ADULT NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 1.OOE-05 1.66E-07 1.41E-07 0. 0. 2.04E-05 0. 2.45E-07 SN-126 6.16E+09 1.37E+08 3.99E+07 0. 5.16E+07 8.84E+09 0. 2.23E+08 SB-124 1.04E+08 1.97E+06 2.51E+05 0. 8.06E+07 2.94E+09 0. 4.10E+07 SB-125 1.94E+08 1.06E+07 7.39E+07 9.77E+07 1.78E+10 1.59E+09 0. 3.73E+07 TE-125M 9.65E+07 3.51E+07 2.91E+07 3.93E+08 0. 3.85E+08 0. 1.29E+07 TE-127M 3.50E+08 1.22E+08 9.18E+07 1.42E+09 0. 1.59E+09 0. 4.31E+07 TE-129M 2.55E+08 9.54E+07 8.79E+07 1.06E+09 0. 1.28E+09 0. 4.05E+07 1-130 3.93E+05 1.16E+06 1.48E+08 1.81 E+06 0. 9.98E+05 0. 4.58E+05 1-131 8.83E+07 1.16E+08 3.79E+10 1.98E+08 0. 3.05E+07 0. 6.63E+07 1-132 5.57E+01 1.49E+02 1.96E+04 2.38E-02 0. 2.80E+01 0. 5.29E+01 1-133 2.13E+06 3.69E+06 7.1OE+08 6.44E+06 0. 3.24E+06 0. 1.13E+06 1-134 1.03E-04 2.79E-04 3.63E-02 4.45E-04 0. 2.43E-07 0. 9.99E-05 1-135 4.04E+04 1.07E+05 1.40E+07 1.70E+05 6.27E-02 1.19E+05 0. 3.91E+04 CS-134 4.87E+09 1.11E+10 0. 3.61E+09 1.19E+09 1.94E+08 0. 9.09E+09 CS-136 4.20E+07 1.66E+08 0. 9.23E+07 1.27E+07 1.89E+07 0. 1.19E+08 CS-137 6.37E+09 8.70E+09 0. 2.96E+09 9.81E+08 1.67E+08 0. 5.71E+09 BA-140 1.29E+08 1.70E+05 0. 5.50E+04 9.25E+04 8.54E+08 0. 8.48E+06 CE-141 1.98E+05 1.34E+05 0. 6.19E+04 0. 5.09E+08 0. 1.51E+04 CE-144 3.30E+07 1.38E+07 0. 8.16E+06 0. 1.11E+10 0. *1.77E+06 PR-143 6.35E+04 2.55E+04 0. 1.47E+04 0. 2.78E+08 0. 3.15E+03 ND-i 47 9.68E+04 4.50E+04 0. 3.40E+04 0. 1.95E+08 0. 4.73E-03 BASED ON 1 1.Ci/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, XjQ, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B -41 11/22/02

¶;

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - Fresh and Stored Fruits and Vegetables AGE GROUP - TEENAGER NUCLIDE ORGAN DOSE (SQ METER - MREH/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 2.57E+03 2.57E+03 3.24E+03 2.57E+03 2.57E+03 0. 2.57E+03 C-14 2.71E+05 2.71E+05 2.71E+05 2.03E+05 2.71E+05 2.71E+05 0. 2.71E+05 P-32 1.13+09 7.06E+07 0. 0. 0. 1.27E+08 0. 4.36E+07 CR-51 0. 0. 2.74E+04 1.01E+04 6.08E-04 1.15E+07 0. 4.58E+04 MN-54 0. 3.52E+08 0. 1.05E+08 0. 1.08E+09 0. 6.72E+07 FE-59 1.34E+08 3.18E+08 0. 0. 8.80E+07 1.05E+09 0. 1.21E+08 CO-57 0. 1.31E+07 0. 0. 0. 3.34E+08 0. 2.19E+07 CO-54 0. 4.45E+07 0. 0. 0. 6.02E+08 0. 1.02E+08 CO-60 0. 2.44E+08 0. 0. 0. 2.93E+09 0. 5.57E+08 NI-63 1.18E-10 8.18E+08 0. 0. 0. 1.71E+08 0. 3.96E+08 ZN-65 3.57E+08 1.14E+09 0. 7.57E+08 0. 7.13E+08 0. 5.12E+08 RB-86 0. 1.94E+08 0. 0. 0. 3.83E+07 0. 9.06E+07 SR-89 1.58E+10 0. 0. 0. 0. 1.72E+09 0. 4.55E+08 SR-90 9.40E+1 1 0. 0. 0. 3.36E+09 2.97E+10 0. 2.33E+11 Y-91 7.69E+06 0. 0. 0. 0. 2.95E+09 0. 2.06E+05 ZR-95 1.87E+06 7.03E+05 0. 7.90E+05 0. 1.86E+09 0. 4.66E+05 NB-95 1.69E+05 1.02E+05 0. 8.OOE+04 0. 4.15E+08 0. 5.73E+04 RU-103 6.46E+06 0. 0. 1.93E+07 0. 5.04E+08 0. 2.89E+06 RU-106 3.15E+08 0. 0. 4.20E+08 0. 1.43E+10 0. 3.96E+07 AG-1I0M 1.19E+07 1.1OE+07 0. 2.17E+07 0. 4.50E+09 0. 6.56E+06 CD-1 15M 0. 5.41 E+07 0. 4.29E+07 0. 2.28E+09 0. 1.73E+06 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, XJQ, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B - 42 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - Fresh and Stored Fruits and Vegetables AGE GROUP - TEENAGER NUCLIDE ORGAN DOSE (SQ. METER MREH/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 9.25E-06 1.53E-07 1.22E-07 0. 0. 1.33E-05 0. 2.28E-07 SN-126 7.79E+09 1.54E+08 4.53E+07 0. 6.01E+07 1.02E+10 0. 2.54E+08 SB-124 1.12E+08 2.11E+06 2.71E+05 0. 8.69E+07 3.17E+09 0. 4.42E+07 SB-125 2.33E+08 1.66E+07 1.16E+07 1.15E+08 2.01E+10 1.82E+09 0. 4.40E+07 TE-125M 1.48E+08 5.30E+07 4.18E+07 4.22E+08 0. 4.14E+08. 0. 1.97E+07 TE-127M 3.88E+08 1.36E+08 1.03E+08 1.56E+08 0. 1.95E+09 0. 4.81E+07 TE-129M 3.74E+08 1.39E+08 1.20E+08 1.08E+09 0. 1.31E+09 0. 5.90E+07 1-130 2.58E+05 7.64E+05 9.72E+07 1.19E+06 0. 6.55E+05 0. 3.OOE+05 1-131 7.33E+07 1.03E+08 2.99E+10 1.34E+08 0. 1.96E+07 0. 6.17E+07 1-132 3.65E+01 9.77E+01 1.29E+04 1.56E+02 0. 1.84E+01 0. 3.47E+01 1-133 1.98E+06 3.36E+06 6.1OE+08 4.23E+06 0. 2.44E+06 0. 1.04E+06 1-134 6.75E-05 1.83E-04 2.38E-02 2.92E-04 0. 1.60E-07 0. 6.56E-05 1-135 2.65E+04 7.OOE+04 9.15E+06 1.11E+05 7.12E-02 7.84E+04 0. 2.57E+04 CS-134 6.84E+09 1.65E+10 0. 4.08E+09 2.00E+09 1.90E+08 0. 7.69E+09 CS-136 3.25E+07 1.28E+08 0. 7.13E+07 9.78E+06 1.46E+07 0. 9.21E+07 CS-137 9.68E+09 1.31E+10 0. 3.35E+09 1.73E+09 1.74E+08 0. 4.57E+09 BA-140 1.33E+08 1.78E+05 0. 4.22E+04 1.13E+05 4.94E+08 0. 8.86E+06 CE-141 2.68E+05 1.79E+05 0. 6.25E+04 0. 4.87E+08 0. 2.07E+04 CE-144 5.47E+07 2.25E+07 0. 9.17E+06 0. 1.29E+10 0. 2.91E+06 PR-143 5.OOE+04 2.20E+04 0. 1.16E+04 0. 2.19E+08 0. 2.49E+03 ND-147 9.80E+04 3.55E+04 0. 2.97E+04 0. 1.45E+08 0. 4.50E+03 BASED ON 1 VICi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, XdQ, AND D/Q.

NOTE -THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B - 43 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION, MANUAL 3.0 RADIOACTIVE GA SEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - Fresh and Stored Fruits and Vegetables "

AGE GROUP - CHILD NUCLIDE ORGAN DOSE (SQ.METER-MREM/YR PER UCI/SEC) _,,___

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 3.98E+03 3.98E+03 2.62E+03 3.98E+03 3.98E+03 0. 3.98E+03 C-14 6.54E+05 .6.54E+05 6.54E+05 1.65E+05 6.54E+05 6.54E+05 0. 6.54E+05 P-32 7.89E+08 4.94E+07 0. 0. -"; 0. 8.87E+07 0. 3.05E+07 CR-51 0. 0. 2.1OE+04 7.76E+03 4.67E+04 8.84E+06 0. 3.51E+04 MN-54 0. 2.84E+08 0. 8.45E+07 0. 8.70E+08 0. 5.42E+07 FE-59 1.05E+08 2.50E+08 0. 0. 6.95E+07 8.26E+08 0. 9.52E+07 CO-57 0. 1.06E+07 0. 0. 0. 2.69E+08 0. 1.77E+07 CO-58 0. 6.62E+07 0. 0. 0. 3.94E+08 0. 2.OOE+08 CO-60 0. 3.69E+08 0. 0. 0. 2.05E+09 0. 1.11E+09 NI-63 9.54E+09 6.62E+08 0. 0. 0. 1.38E+08 0. 3.20E+08 ZN-65 2.88E+08 9.12E+08 0. .6.1OE+08 0. 5.75E+08 0. 4.13E+08 RB-86 0. 1.43E+08 0. 0. 0. 2.82E+07 0. 6.66E+07 SR-89 3.76E+10 0. 0. 0. 0. 1.40E+09 0. 1.08E+09 SR-90 1.26E+12 0. 0. 0. 0. 2.54E+10 0. 3.19E+11 Y-91 1.82E+07 0. 0. 0. 0. 2.42E+09 0. 4.87E+05 ZR-95 4.15E+06 1.09E+06 0. 6.33E+05 0. 1.32E+09 0. 9.43E+05 NB-95 3.55E+05 1.51E+05 0. 6.24E+04 0. 2.26E+08 0. 1.11E+05 RU-103 1.45E+07 0. 0. 1.51E+07 0. 3.81E+08 0. 5.86E+06 RU-106 7.57E+08 0. 0. 3.38E+08 0. 1.18E+10 0. 9.42E+07 AG-110M 9.61E+06 8.89E+06 0. 1.75E+07 0. 3.63E+09 0. 5.29E+06 CD-115M 0. 4.26E+07 0. 3.38E+07 0. 1.79E+09 0. 1.36E+06 BASED ON 1 ýtCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR ,/Q, Xd/Q, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B - 44 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - Fresh and Stored Fruits and Vegetables AGE GROUP - CHILD NUCLIDE ORGAN DOSE (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 1.71E-05 2.14E-07 2.26E-07 0. 0. 8.503-06 0. 4.21E-07 SN-126 6.29E+09 1.25E+08 3.66E+07 0. 4.91E+07 8.33E+09 0. 2.06E+08 SB-124 8.90E+07 1.68E+06 2.15E+05 0. 6.90E+07 2.52E+09 0. 3.51E+07 SB-125 2.54E+08 2.86E+07 2.80E+07 9.47E+07 1.62E+10 1.46E+09 0. 4.44E+07 TE-125M 3.50E+08 9.50E+07 9.84E+07 3.35E+08 0. 3.38E+08 0. 4;67E+07 TE-127M 3.25E+08 1.12E+08 9.15E+07 1.26E+09 0. 1.87E+09 0. 4.14E+07 TE-129M 8.69E+08 2.42E+08 2.77E+08 8.43E+08 0. 1.05E+09 0. 1.34E+08 1-130 1.60E+05 4.73E+05 6.02E+07 7.35E+05 0. 4.05E+05 0. 1.86E+05 1-131 1.36E+08 1.39E+08 4.52E+10 8.48E+07 0. 1.19E+07 0. 1.05E+08 1-132 2.26E+01 6.05E+01 7.97E+03 9.65E+01 0. 1.14E+01 0. 2.15E+01 1-133 3.61 E+06 4.46E+06 1.08E+09 2.62E+06 0. 1.81 E+06 0. 1.75E+06 1-134 4.18E+05 1.14E+04 1.47E-02 1.81E-04 0. 9.89E-08 0. 4.06E-05 1-135 1.64E+04 4.33E+04 5.67E+06 6.89E+04 5.75E-02 4.85E+04 0. 1.59E+04 CS-134 1.54E+10 2.59E+10 0. 3.29E+09 2.88E+09 1.40E+08 0. 5.51E+09 CS-1 36 2.23E+07 8.80E+07 0. 4.90E+07 6.72E+06 1.OOE+07 0. 6.34E+07 CS-137 2.28E+10 2.21E+10 0. 2.72E+09 2.59E+09 1.34E+08 0. 3.29E+09 BA-140 2.76E+08 2.54E+05 0. 2.89E+04 1.44E+05 3.60E+08 0. 1.62E+07 CE-141 6.21 E+05 3.1OE+05 0. 4.85E+04 0. 3.89E+08 0. 4.62E+04 CE-144 1.31E+08 4.1OE+07 0. 7.39E+06 0. 1.06E+10 0. 6.97E+06 PR-143 3.48E+04 1.40E+04 0. 8.03E+03 0. 1.52E+08 0. 1.72E+03 N _D-147 7.61 E+04 2.46E+04 1 0. 2.17E+04 , . -8+ 0 . 3 40E+03 BASED ON 1 jtCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, XJQ, AND D/Q.

NOTE - THE UNITS FOR C-14 AND H-3 ARE (MREM/YR PER UCI/CU.METER) 3B - 45 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - Stored Fruits and Vegetables AGE GROUP - ADULT NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREMIYR PER UCI/SEC)

BONE LIVER - THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 2.46E+03 2.46E+03 2.46E+03 2.46E+03, 2.46E+03 0. 2.46E+03 C-14 7.72E+05 1.55E+05 1.55E+05 1.55E+05 1.55E+05 1.55E+05 0. 1.55E+05 P-32 3.67E+08 2.30E+07 0. 0. 0. 4.13E+07 0. 1.42E+07 CR-51 0. 0. 1.63E+04 6.03E+03 3.63E+04 6.87E+06 0. 2.73E+04 MN-54 0. 2.64E+08 0. 7.86E+07 0. 8,09E+08 0. 5.04E+07 FE-59 9.06E+07 2.15E+08 0. 0. 5.97E+07 7.10E+08 0. 8.18E+07 CO-57 0. 9.85E+06 0. 0. 0. 2.50E+08 0. 1.64E+07 CO-58 0. 2.39E+07 0. 0. 0. 4.84E+08 0. 5.36E+07 CO-60 0. 1.44E+08 0. 0. 0. 2.69E+09 0. 3.16E+08 NI-63 8.95E+09 6.21E+08 0. 0. 0. 1.29E+08 0. 3.OOE+08 ZN-65 2.67E+08 8.46E+08 0. 5.66E+08 0. 5.33E+08 0. 3.83E+08 RB-86 0. 9.OOE+07 0. 0. 0. 1.78E+07 0. 4.20E+07 SR-89 7.34E+09 0. 0. 0. 0. 1.17E+09 0. 2.10E+08 SR-90 5.22E+11 0. 0. 0. , 0. 1.40E+10 0. 1.28E+11 Y-91 3.88E+06 0. 0. 0.,:, 0. 2.14E+09 0. 1.04E+05 ZR-95 1.11E+06 4.04E+05 0. 5.72E+05 0. 1.59E+09 0. 2.42E+05 NB-95 9.35E+04 5.19E+04 0. 5.15E+04 0. 3.15E+08 0. 2.04E+04 RU-103 3.34E+06 0. 0. 1.28E+07 0. 3.90E+08 0. 1.44E+06 RU-106 1.63E+08 0. 0. 3.1,5E+08 0. 1.06E+10 0. 2.06E+07 AG-110M 8.92E+06 8.25E+06 0. 1.'62E+07 0. 3.37E+09 0. 4.91E+06 CD-115M 0. 3.64E+07 0. 2,89E+07 0. 1.53E+09 0. 1.16E+06 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR XJQ, xd/Q, AND D/Q.

3B - 46 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - Stored Fruits and Vegetables AGE GROUP - ADULT NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 0. 0. 0. 0. 0. 0. 0. 0.

SN-126 5.91E+09 1.18E+08 3.44E+07 0. 4.73E+07 7.99E+09 0. 1.94E+08 SB-124 7.88E+07 1.49E+06 1.90E+05 0. 6.11E+07 2.23E+09 0. 3.11E+07 SB-125 1.68E+08 9.84E+06 6.99E+06 9.26E+07 1.52E+10 1.37E+09 0. 3.23E+07 TE-125M 7.27E+07 2.64E+07 2.19E+07 2.96E+08 0. 2.90E+08 0. 9.74E+06 TE-127M 2.82E+08 9.87E+07 7.41E+07 1.15E+09 0. 1.28E+09 0. .3.48E+07 TE-124M 1.25E+08 6.20E+07 5.72E+07 6.92E+08 0. 8.32E+08 0. 2.63E+07 1-130 0. 0. 0. 0. 0. 0. 0. 0.

1-131 2.99E+06 4.28E+06 1.40E+09 7.33E+06 0. 1.13E+06 0. 2.45E+06 1-132 0. 0. 0. 0. 0. 0. 0. 0.

1-133 0. 0. 0. 0. 0. 0. 0. 0.

1-134 0. 0. 0. 0. 0. 0. 0. ,0.

1-135 5.14E-01 4.74E-01 0. 1.80E-01 5.40E-02 1.11E-02 0. 2.11E-01 CS-1 34 3.99E+09 9.50E+09 0. 3.08E+09 1.02E+09 1.66E+08 0. 7.76E+09 CS-1 36 8.82E+06 3.48E+07 0. 1.94E+07 2.66E+06 3.96E+06 0. 2.51 E+07 CS-137 5.48E+09 7.48E+09 0. 2.55E+09 8.44E+08 1.44E+08 0. 4.91E+09 BA-140 2.60E+07 3.45E+04 0. 1.11E+04 1.87E+04 1.89E+08 0. 1.71E+06 CE-141 1.26E+05 8.50E+04 0. 3.94E+04 0. 3.24E+08 0. 9.63E+03 CE-144 2.78E+07 1.16E+07 0. 6.87E+06 0. 9.37E+09 0. 1.49E+06 PR-143 1.51 E+04 6.06E+03 0. 3.49E+03 0. 6.60E+07 0. 7.49E+02 ND-147 6.19E+04 1.06E+04 0. 1.33E+04 0. 3.19E+07 0. 2.49E+03 BASED ON 1 pICi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR x./Q, XdQ, AND D/Q.

3B1-47 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - Stored Fruits and Vegetables AGE GROUP - TEENAGER NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM1YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 2.36E+03 2.36E+03 2.98E+03 2.36E+03 2.36E+03 0. 2.36E+03 C-14 2.49E+05 2.49E+05 2.49E+05 1.87E+05 2.49E+05 2.49E+05 0. 2.49E+05 P-32 4.45E+08 2.79E+07 0. 0. 0. 5.OOE+07 0. 1.72E+07 CR-51 0. 0. 1.98E+04 7.31 E+03 4.40E+04 8.33E+06 0. 3.31 E+04 MN-54 0. 3.20E+08 0. 9.52E+07 0. 9.80E+08 0. 6.11E+07 FE-59 1.10E+08 2.61E+08 0. 0. 7.23E+07 8.60E+08 0. 9.91E+07 CO-57 0. 1.19E+07 0. 0. 0. 3.03E+08 0. 1.99E+07 CO-58 0. 3.85E+07 0. 0. 0. 5.21 E+08 0. 8.78E+07 CO-60 0. 2.24E+08 0. 0. 0. 2.69E+09 0. 5.11E+08 NI-63 1.08E+10 7.52E+08 0. 0. 0. 1.57E+08 0. 3.64E+08 ZN-65 3.23E+08 1.03E+09 0. 6.86E+08 0. 6.46E+08 0. 4.64E+08 RB-86 0. 1.09E+08 0. 0. 0. 2.15E+07 0. .5.09E+07 SR-89 1.32E+10 0. 0. 0. 0. 1.44E+09 0. 3.80E+08 SR-90 8.64E+ 11 0. 0. 0. 3.12E+09 2.74E+10 0. 2.14E+11 Y-91 6.54E+06 0. 0. 0. 0. 2.51E+09 0. 1.75E+05 ZR-95 1.63E+06 6.21E+05 0. 6.92E+05 0. 1.67E+09 0. 4.1OE+05 NB-95 1.32E+05 7.93E+04 0. 6.24E+04 0. 3.24E+08 0. 4.47E+04 RU-103 5.19E+06 0. 0. 1.55E+07 0. 4.05E+08 0. 2.32E+06 RU-106 2.87E+08 0. 0. 3.28E+08 0. 1.30E+10 0. 3.61E+07 AG-110M 1.08E+07 1.OOE+07 0. 1.97E+07 0. 4.08E+09 0. 5.95E+06 CD-115M 0. 4.41E+07 0. 3.50E+07 0. 1.86E+09 0. 1.41E+06 BASED ON 1 CiCVSEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, xJQ, AND D/Q.

ý3B3- 48 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - Stored Fruits and Vegetables AGE GROUP - TEENAGER NUCLIDE ORGAN DOSE FACTORS (SQ. METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 0. 0. 0. 0. 0. 0. 0. 0.

SN-126 7.16E+09 1.42E+08 4.17E+07 0. 5.73E+07 9.67E+09 0. 2.35E+08 SB-124 9.55E+07 1.80E+06 2.31E+05 0. 7.41E+07 2.70E+09 0. 3.77E+07 SB-125 2.15E+08 1.60E+07 1.13E+07 1.12E+08 1.84E+10 1.67E+09 0. 4.06E+07 TE-125M 1.26E+08 4.50E+07 3.55E+07 3.58E+08 0. 3.52E+08 0. 1.67E+07 TE-127M 3.43E+08 1.21E+08 9.09E+07 1.38E+09 0. 1.73E+09 0. 4.26E+07 TE-129M 2.90E+08 1.07E+08 9.27E+07 8.38E+08 0. 1.01E+09 0. 4.56E+07 1-130 0. 0. 0. 0. 0. 0. 0. 0.

1-131 4.85E+06 6.85E+06 1.98E+09 8.88E+06 0. 1.30E+06 0. 4.08E+06 1-132 0. 0. 0. 0. 0. 0. 0. 0.

1-133 0. 0. 0. 0. 0. 0. 0. 0.+

1-134 0. 0. 0. 0. 0. 0. 0. 0.

1-135 6.23E-01 5.75E-01 0. 2.18E-01 6.55E-02 1.34E-02 0. 2.55E-01 CS-134 6.26E+09 1.51E+10 0. 3.73E+09 1.83E+09 1.74E+08 0. 7.04E+09 CS-136 1.07E+07 4.22E+07 0. 2.35E+07 3.22E+06 4.79E+06 0. 3.04E+07 CS-137 8.90E+09 1.20E+10 0. 3.08E+09 1.59E+09 1.60E+08 0. 4.20E+09 BA-140 4.38E+07 5.70E+04 0. 1.34E+04 3.61 E+04 1.75E+08 0. 2.82E+06 CE-141 2.05E+05 1.37E+05 0. 4.78E+04 0. 3.72E+08 0. 1.58E+04 CE-144 4.97E+07 2.04E+07 0. '8.33E+06 0. 1.17E+10 0. 2.64E+06 PR-143 1.83E+04 7.35E+03 0. 4.23E+03 0. 8.OOE+07 0. 9.07E+02 ND-147 7.51E+04 1.29E+04 0. 1.61 E+04 0. 3.86E+07 0. 3.03E+03 BASED ON 1 gCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, Xd1Q, AND D/Q.

3B - 49 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - Stored Fruits and Vegetables AGE GROUP - CHILD NUCLIDE ORGAN DOSE FACTORS (SQ. METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 3.73E+03 3.73E+03 2.46E+03 3.73E+03 3.73E+03 0. 3.73E+03 C-14 6.14E+05 6.14E+05 6.14E+05 1.55E+05 6.14E+05 6.14E+05 0. 6.14E+05 P-32 3.67E+08 2.30E+07 0. 0. 0. 4.13E+07 0. 1.42E+07 CR-51 0. 0. 1.63E+04 6.03E+03 3.63E+04 6.87E+06 0. 2.73E+04 MN-54 0. 2.64E+08 0. 7.86E+07 0. 8.09E+08 0. 5.04E+07 FE-59 9.06E+07 2.15E+08 0. 0. 5.97E+07 7.1OE+08 0. 8.18E+07 CO-57 0. 9.85E+06 0. 0. 0. 2.50E+08 0. 1.64E+07 CO-58 0. 5.93E+07 0. 0. 0. 3.53E+08 0. 1.79E+08 CO-60 0. 3.46E+08 0. 0. 0. 1.92E+09 0. 1.04E+09 NI-63 8.95E+09 6.21E+08 0. 0. 0. 1.29E+08 0. 3.00E+08 ZN-65 2.67E+08 8.46E+08 0. 5.66E+08 0. 5.33E+08 0. 3.83E+08 RB-86 0. 9.OOE+07 0. 0. 0. 1.78E+07 0. 4.20E+07 SR-89 3.28E+10 0. 0. 0. 0. 1.22E+09 0. 9.38E+08 SR-90 1.18E+12 0. 0. 0. 0. 2.39E+10 0. 2.99E+11 Y-91 1.61E+07 0. 0. 0. 0. 2.14E+09 0. 4.30E+05 ZR-95 3.74E+06 9.93E+05 0. 5.72E+05 0. 1.21 E+09 0. 8.55E+05 NB-95 2.93E+05 1.25E+05 0. 5.15E+04 0. 2.16E+08 0. 9.17E+04 RU-103 1.23E+07 0. 0. 1.28E+07 0. 3.22E+08 0. 4.95E+06 RU-106 7.05E+08 0. 0. 3.15E+08 0. 1.10E+10 0. 8.77E+07 AG-110M 8.92E+06 8.25E+06 0. 1.62E+07 0. 3.37E+09 0. 4.91E+06 CD-115M 0. 3.64E+07 0. 2.89E+07 0. 1.53E+09 0. 1.16E+06 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, XJQ, AND D/Q.

3B - 50 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - Stored Fruits and Vegetables AGE GROUP - CHILD NUCLIDE ORGAN DOSE FACTORS (SQ. METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 0. 0. 0. 0. 0. 0. 0. 0.

SN-126 5.91E+09 1.18E+08 3.44E+07 0. 4.73E+07 7.99E+09 0. 1.94E+08 SB-124 7.88E+07 1.49E+06 1.90E+05 0. 6.11E+07 2.23E+09 0. 3.11E+07 SB-125 2.42E+08 2.79E+07 " 2.73E+07 9.26E+07 1.52E+10 1.37E+09 0. 4.21 E+07 TE-125M 3.09E+08 8.38E+07 8.68E+07 2.96E+08 0. 2.98E+08 0. 4.12E+07 TE-127M 2.96E+08 1.02E+08 8.34E+07 1.15E+09 0. 1.71E+09 0. 3.77E+07 TE-129M 7.12E+08 1.98E+08 2.27E+08 6.92E+08 0. 8.57E+08 0. 1.10E+08 1-130 0. 0. 0. 0. 0. 0. 0. 0.

1-131 1.17E+07 1.20E+07 3.90E+09 7.33E+06 0. 1.03E+06 0. 9.05E+06 1-132 0. 0. 0. 0. 0. 0. 0. 0.

1-133 0. 0. 0. 0. 0. 0. 0. 0.

1-,134 0. 0. 0. 0. 0. 0. 0. 0.

1-135 5.14E-01 4.74E-01 0. 1.80E-01 5.40E-02 1.11E-02 0. 2.11E-01 CS-134 1.44E+10 2.42E+10 0. 3.08E+09 2.69E+09 1.31E+08 0. 5.15E+09 CS-136 8.82E+06 3.48E+07 0. 1.94E+07 2.66E+06 3.96E+06 0. 2.51E+07 CS-137 2.14E+10 2.07E+10 0. 2.55E+09 2.43E+09 1.26E+08 0. 3.09E+09 BA-140 1.06E+08 9.79E+04 0. 1.11E+04 5.52E+04 1.52E+08 0. 6.20E+06 CE-141 5.04E+05 2.52E+05 0. 3.94E+04 0. 3.16E+08 0. 3.75E+04 CE-144 1.22E+08 3.81E+07 0. 6.87E+06 0. 9.89E+09 0. 6.48E+06 PR-143 1.51 E+04 6.06E+03 0. 3.49E+03 0. 6.60E+07 0. 7.49E+02 ND-147 6.19E+04 1.06E+04 0. 1.33E+04 0. 3.19E+07 0. 2.49E+03 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, xJQ, AND D/Q.

-.3B - 51 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - FRESH FRUITS AND VEGETABLES AGE GROUP -ADULT NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 4.02E+02 4.02E+02 4.02E+02 4.02E+02 4.02E+02 0. 4.02E+02 C-14 1.25E+05 2.50E+04 2.50E+04 2.50E+04 2.50E+04 2.50E+04 0. 2.50E+04 P-32 1.04E+09 6.51E+07 0. 0. 0. 1.17E+08 0. 4.02E+07 CR-51 0. 0. 1.15E+04 4.25E+03 2.56E+04 4.85E+06 0. 1.93E+04 MN-54 0. 4.87E+07 0. 1.45E+07 0. 1.49E+08 0. 9.31E+06 FE-59 3.64E+07 8.64E+07 0. 0. 2.40E+07 2.85E+08 0. 3.29E+07 CO-57 0. 1.85E+06 0. 0. 0. 4.70E+07 0. 3.08E+06 CO-58 0. 6.89E+06 0. 0. 0. 1.40E+08 0. 1.54E+07 00-60 0. 2.38E+07 0. 0. 0. 4.46E+08 0. 5.23E+07 NI-63 1.45E+09 1.01E+08 0. 0. 0. 2.1OE+07 0. 4.87E+07 ZN-65 5.11E+07 1.62E+08 0. 1.09E+08 0. 1.02E+08 0. 7.34E+07 RB-86 0. 1.30E+08 0. 0. 0. 2.56E+07 0. 6.06E+07 SR-89 2.67E+09 0. 0. 0. 0. 4.26E+08 0. 7.64E+07 SR-90 8.49E+10 0. 0. 0. 0. 2.14E+09 0. 2.07E+10 Y-91 1.26E+06 0. 0. 0. 0. 6.92E+08 0. 3.37E+04 ZR-95 2.93E+05 9.82E+04 0. 1.49E+05 0. 3.34E+08 0. 6.38E+04 NB-95 4.87E+04 2.71E+04 0. 2.68E+04 0. 1.64E+08 0. 1.06E+04 RU-103 1.50E+06 0. 0. 5.75E+06 0. 1.76E+08 0. 6.49E+05 RU-106 2.95E+07 0. 0. 5.71E+07 0. 1.91E+09 0. 3.74E+06 AG-110M 1.69E+06 1.56E+06 0. 3.08E+06 0. 6.38E+08 0. 9.30E+05 CD-115M 0. 1.53E+07 0. 1.21E+07 0. 6.42E+08 0. 4.88E+05 BASED ON 1 p.Ci/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X'/Q, XdIQ, AND D/Q.

3B - 52 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - FRESH FRUITS AND VEGETABLES AGE GROUP - ADULT NUCLIDE ORGAN DOSE FACTORS (SQ. METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 1.OOE-05 1.66E-07 1.41 E-07 0.1 0. 2.04E-05 0. 2.45E-07 SN-126 4.52E+08 1.89E+07 5.54E+06 0. 4.31E+06 8.46E+08 0. 2.94E+07 SB-124 2.52E+07 4.75E+05 6.08E+04 0. 1.95E+07 7.12E+08 0. 9.94E+06 SB-125 2.58E+07 7.23E+05 4.03E+05 5.14E+06 2.56E+09 2.22E+08 0. 5.1OE+06 TE-125M 2.38E+07 8.65E+06 7.17E+06 9.69E+07 0. 9.51E+07 0. 3.19E+06 TE-127M 6.75E+07 2.36E+07 1.77E+07 2.73E+08 0. 3.06E+08 0. 8.32E+06 TE-129M 8.93E+07 3.34E+07 3.08E+07 3.73E+08 0. 4.49E+08 0. 1.42E+07 1-130 3.93E+05 1.16E+06 1.48E+08 1.81 E+06 0. 9.98E+05 0. 4.58E+05 1-131 7.78E+07 1.12E+08 3.65E+10 1.91 E+08 0. 2.94E+07 0. .6.38E+07 1-132 5.57E+01 1.49E+02 1.96E+04 2.38E+02 0. 2.80E+01 0. 5;29E+01 1-133 2.13E+06 3.69E+06 7.1OE+08 6.44E+06 0. 3.24E+06 0. 1.13E+06 1-134 1.03E-04 2.79E-04 3.63E-02 4.45E-04 0. 2.43E-07 0. 9.99E-05 1-135 4.04E+04 1.07E+05 1.40E+07 1.70E+05 8.65E-03 1.19E+05 0. 3.91E+04 CS-1 34 6.82E+08 1.62E+09 0. 5.26E+08 1.74E+08 2.84E+07 0. 1.33E+09 CS-136 3.32E+07 1.31 E+08 0. 7.29E+07 9.99E+06 1.49E+07 0. 9.43E+07 CS-1 37 8.90E+08 1.22E+09 0. 4.14E+08 1.37E+08 2.34E+07 0. 7.98E+08 BA-140 1.03E+08 1.35E+05 0. 4.39E+04 7.38E+04 6.65E+08 0. 6.77E+06 CE-141 7.16E+04 4.85E+04 0. 2.25E+04 0. 1.85E+08 0. 5.49E+03 CE-144 5.19E+06 2.17E+06 0. 1.29E+06 0. 1.75E+09 0. 2.78E+05 PR-143 4.84E+04 1.94E+04 0. 1.12E+04 0. 2.12E+08 0. 2.40E+03 ND-147 3.49E+04 3.43E+04 0. 2.07E+04 0. 1.63E+08 0. 2.24E+03 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, XJQ, AND D/Q.

3B - 53 11/22/02

TURKEY POINT UNIT 3 DOSE CALCULATION MANUAL.

3.0 RADIOACTIVE GASEOUS EFFLUENTS ; I ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - FRESH FRUITS AND VEGETABLES AGE GROUP - TEENAGER NUCLIDE ORGAN DOSE FACTORS (SQ. METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY H-3 0. 2.09E+02 2.09E+02 2.64E+02 2.09E+02 2.09E+02 0. 2.09E+02 C-14 2.18E+04 2.18E+04 2.18E+04 1.64E+04 2.18E+04 2.18E+04 0. 2.18E+04 P-32 6.81 E+08 4.27E+07 0. 0. 0. 7.66E+07 0. 2.64E+07 CR-51 0. 0. 7.56E+03 2.79E+03 1.68E+04 3.18E+06 0. 1.27E+04 MN-54 0. 3.20E+07 0. 9.52E+06 0. 9.80E+07 0. 6.11E+06 FE-59 2.39E+07 5.67E+07 0. 0. 1.57E+07 1.87E+07 0. 2.16E+07 CO-57 0. 1.22E+06 0. 0. 0. 3.09E+07 0. 2.02E+06 CO-58 0. 6.01E+06 0. 0. 0. 8.12E+07 0. 1.37E+07 CO-60 0. 2.01 E+07 0. 0. 0. 2.41 E+08 0. 4.58E+07 NI-63 9.52E+08 6.61E+07 0. 0. 0. 1.38E+07 0. 3.19E+07 ZN-65 3.35E+07 1.06E+08 0. 7.12E+07 0. 6.70E+07 0. 4.82E+07 RB-86 0. 8.52E+07 0. 0. 0. 1.68E+07 0. 3.97E+07 SR-89 2.61E+09 0. 0. 0. 0. 2.83E+08 0. 7.48E+07 SR-90 7.61E+10 0. 0. 0. 2.41E+08 2.31 E+09 0. 1.88E+10 Y-91 1.15E+06 0. 0. 0. 0. 4.41E+08 0. 3.06E+04 ZR-95 2.35E+05 8.19E+04 0. 9.81E+04 0. 1.92E+08 0. 5.61E+04 NB-95 3.72E+04 2.24E+04 0. 1.76E+04 0. 9.14E+07 0. 1.26E+04 RU-103 1.27E+06 0. 0. 3.77E+06 0. 9.87E+07 0. 5.66E+05 RU-106 2.82E+07 0. 0. 3.75E+07 0. 1.28E+09 0. 3.54E+06 AG-110M 1.11E+06 1.03E+06 0. 2.02E+06 0. 4.19E+08 0. 6.1OE+05 CD-115M 0. 1.OOE+07 0. 7.94E+06 0. 4.21E+08 0. 3.20E+05 BASED ON 1 piCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, Xd/Q, AND D/Q.

3B - 54 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - FRESH FRUITS AND VEGETABLES AGE GROUP -TEENAGER _

NUCLIDE ORGAN DOSE FACTORS (SQ. METER-MREH/YR PER UCI/SEC)

BONE LIVER THYROID! KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 9.25E-06 1.53E-07 1.22E-07 0., 0. 1.33E-05 0. 2.28E-07 SN-126 6.25E+08 1.24E+07 3.64E+06 0., 2.83E+06 5.55E+08 0. 1.94E+07 SB-124 1.65E+07 3.12E+05 3.99E+04 0. 1.28E+07 4.67E+08 0. 6.53E+06 SB-125 1.73E+07 5.97E+05 3.48E+05 3.38E+06 1.68E+09 1.45E+08 0. 3.40E+06 TE-125M 2.23E+07 7.99E+06 6.30E+06 6.36E+07 0. 6.24E+07 0. 2.96E+06 TE-127M 4.46E+07 1.55E+07 1.18E+07 1.80E+08 0. 2.23E+08 0. 5.51E+06 TE-129M 8.46E+07 3.14E+07 2.71E+07 2.45E+07 0. 2.95E+08 0. 1.33E+07 1-130 2.58E+05 7.64E+05 9.72E+07 1.19E+06 0. 6.55E+05 0. 3.00E+05 1-131 6.84E+07 9.66E+07 2.79E+10 1.25E+08 0. 1.83E+07 0. 5.76E+07 1-132 3.65E+01 9.77E+01 1.29E+04 1656E+02 0. 1.84E+01 0. 3.47E+01 1-133 1.98E+06 3.36E+06 6.10E+08 4.23E+06 0. 2.44E+06 0. 1.04E+06 1-134 6.75E-05 1.83E-04 2.38E-02 2.92E-04 0. 1.60E-07 0. 6.56E-05 1-135 2.65E+04 7.00E+04 9.15E+06 1.11E+05 5.67E-03 7.84E+04 0. 2.57E+04 CS-134 5.79E+08 1.40E+09 0. 3.45E+08 1.69E+08 1.61E+07 0. 6.52E+08 CS-136 2.18E+07 8.60E+07 0. 4.78E+07 6.56E+06 9.77E+06 0. 6.19E+07 CS-137 7.83E+08 1.05E+09 0. 2.72E+08 1.40E+08 1.41 E+07 0. 3.70E+08 BA-140 9.38E+07 1.21 E+05 0. 2.88E+04 7.73E+04 3.19E+08 0. 6.04E+06 CS-141 6.32E+04 4.24E+04 0. 1.47E+04 0. 1.15E+08 0. 4.86E+03 CS-144 5.03E+06 2.06E+06 0. 8.43E+05 0. 1.19E+09 0. 2.67E+05 PR-143 3.17E+04 1.28E+04 0. 7.34E+03 0. 1.39E+08 0. 1.58E+03 ND-147 2.29E+04 2.26E+04 0. 1.36E+04 0. 1.06E+08 0. 1.47E+03 BASED ON 1 pCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR ý/Q, xjQ, AND D/Q.

3B - 55 11/22/02

I 'I TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - FRESH FRUITS AND VEGETABLES AGE GROUP - CHILD NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC)

BONE LIVER THYROID KIDNEY LUNG, 1' GI-LLI SKIN TOTAL BODY H-3 0. 2.47E+02 2.47E+02 1.63E+02 2.47E+02 2.47E+02 0. 2.47E+02 C-14 4.04E+04 4.04E+04 4.04E+04 1.02E+04 4.04E+04 4.04E+04 0. 4.04E+04 P-32 4.22E+08 2.64E+07 0. 0. 0. 4.74E+07 0. 1.63E+07 CR-51 0. 0. 4.68E+03 1.73E+03 1.04E+04 1.97E+06 0. 7.83E+03 MN-54 0. 1.98E+07 0. 5.89E+06 0. 6.07E+07 0. 3.78E+06 FE-59 1.48E+07 3.51E+07 0. 0. 9.75E+06 '1.16E+08 0. 1.34E+07 CO-57 0. 7.53E+05 0. 0. 0. '1.91E+07 0. 1.25E+06 CO-58 0. 6.94E+06 0. 0. 0. . 4.13E+07 0. 2.09E+07 CO-60 0. 2.33E+07 0. 0. 0. 1.29E+08 0. 6.98E+07 NI-63 5.90E+08 4.09E+07 0. 0. 0. 8.53E+06 0. 1.98E+07 ZN-65 2.08E+07 6.59E+07 0. 4.41E+07 0. 4.15E+07 0. 2.98E+07 RB-86 0. 5.28E+07 0. 0. 0. 1.04E+07 0. 2.46E+07 SR-89 4.84E+09 0. 0. 0. 0. 1.81E+08 0. 1.39E+08 SR-90 7.79E+10 0. 0. 0. 0. 1.52E+09 0. 1.98E+10 Y-91 2.12E+06 0. 0. 0. 0. 2.82E+08 0. 5.65E+04 ZR-95 4.06E+05 9.87E+04 0. 6.07E+04 0. 1.08E+08 0. 8.81E+04 NB-95 6.20E+04 2.64E+04 0. 1.09E+04 0. 4.58E+07 0. 1.94E+04 RU-1 03 2.24E-06 0. 0. 2.34E+06 0. 5.88E+07 0. 9.05E+05 RU-1 06 5.19E+07 0. 0. 2.32E+07 0. 8.07E+08 0. 6.46E+06 AG-11iM 6.87E+05 6.36E+05 0. 1.25E+06 0. 2.59E+08 0. 3.78E+05 CD-115M 0. 6.20E+06 0. 4.92E+06 0. 2.61E+08 0. 1.98E+05 BASED ON 1 jCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, X,Q, AND D/Q.

3B - 56 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS ENVIRONMENTAL PATHWAY DOSE CONVERSION FACTORS FOR GASEOUS EFFLUENTS PATHWAY - FRESH FRUITS AND VEGETABLES AGE GROUP - CHILD NUCLIDE ORGAN DOSE FACTORS (SQ.METER-MREM/YR PER UCI/SEC) _

BONE LIVER THYROID KIDNEY LUNG GI-LLI SKIN TOTAL BODY SN-123 1.17E-05 2.14E-07 2.26E-07 0. 0. 8.50E-06 0. 4.21E-07 SN-126 3.87E+08 7.68E+06 2.25E+06 0. 1.75E+06 3.44E+08 0. 1.19E+07 SB-124 1.02E+07 1.93E+05 2.47E+04 0. 7.93E+06 2.89E+08 0. 4.40E+06 SB-1 25 1.22E+07 6.99E+05 6.22E+05 2.09E+06 1.04E+09 9.02E+07 0. 2.29E+06 TE-125M 4.12E+07 1.12E+07 1.16E+07 3.94E+07 0. 3.97E+07 0. 5.49E+06 TE-127M 2.88E+07 9.90E+06 8.09E+06 1.11E+08 0. 1.65E+08 0. 3.67E+06 TE-129M 1.56E+08 4.35E+07 4.99E+07 1.51E+08 0. 1.88E+08 0. 2.41E+07 1-130 1.60E+05 4.73E+05 6.02E+07 7.35E+05 0. 4.05E+05 0. 1.86E+05 1-131 1.24E+08 1.27E+08 4.13E+10 7.75E+07 0. 1.09E+07 0. 9.58E+07 1-132 2.26E+01 6.05E+01 7.97E+03 9.65E+01 0. 1.14E+01 0. 2.15E+01 1-133 3.61E+06 4.46E+06 1.08E+09 2.62E+06 0. 1.81 E+06 0. 1.75E+06 1-134 4.18E-05 1.14E-04 1.47E-02 1.81 E-04 0. 9.89E-08 0. 4.06E-05 1-135 1.64E+04 4.33E+04 5.67E+06 6.89E+04 3.51E-03 4.85E+04 0. 1.59E+04 CS-1 34 9.97E+08 1.68E+09 0. 2.14E+08 1.87E+08 9.08E+06 0. 3.57E+08 CS-136 1.35E+07 5.32E+07 0. 2.96E+07 4.06E+06 6.05E+06 0. 3';83E+07 CS-137 1.41E+09 1.37E+09 0. 1.68E+08 1.60E+08 8.34E+06 0.. 2.04E+08 BA-140 1.70E+08 1.56E+05 0. 1.78E+04 8.87E+04 2.08E+08 0. 9.96E+06 CE-141 1.17E+05 5.84E+04 0. 9.13E+03 0. 7.33E+07 0. 8.69E+03 CE-144 9.23E+06 2.89E+06 0. 5.22E+05 0. 7.51E+08 0. 4.92E+05 PR-143 1.97E+04 7.89E+03 0. 4.54E+03 0. 8.60E+07 0. 9.75E+02 ND-147 1.42E+04 1.39E+04 0. 8.42E+03 0. 6.61 E+07 0. 9.08E+02 BASED ON I 1iCi/SEC RELEASE RATE OF EACH ISOTOPE AND A VALUE OF 1 FOR X/Q, XJQ, AND D/Q.

313-'57, 11/22/02

APPENDIX 3C TECHNICAL BASIS FOR Aeff AND TG 131

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS APPENDIX 3C Technical Bases for Aeff and TG131 Overview The evaluation of doses due to releases of radioactive material to the atmosphere can be simplified by the use of effective dose transfer factors instead of using dose factors which are radionuclide specific. These effective factors, which are based on the typical radionuclide distribution in the releases, can be applied to the total radioactivity released to approximate the dose in the environment, i.e., instead of having to sum the isotopic distribution multiplied by the isotope specific dose factor only a single multiplication (Aeff times the total quantity of radioactive material released) would be needed. This approach provides a reasonable estimate of the actual dose while eliminating the need for a detailed calculational technique.

Determination of Aff The effective dose transfer factor is based on past operating data. The radioactive effluent distribution for the past years can be used to derive a single effective factor by the following equation:

Aeff = Ai f (Eq. 3C-1) where:

Aeff = the effective dose transfer factor A* = the dose transfer factor for radionuclide i f - the fractional abundance of radionuclide i in the radioactive

. effluents---

This equation yields a single dose factor, weighted by the typical radionuclide distribution.

To determine the appropriate effective factor to be used and to evaluate the degree of variability, the atmospheric radioactive effluents for 3 years have been evaluated. An effective dose transfer factor has been determined for the gaseous effluents for all pathways of interest. Tables 3C-1 and 3C-2 present the results of this evaluation.

For the radioiodines and particulates with half-lives greater than 8 days, the effective dose transfer factor is based solely on the radioiodines (1-131, and 1-133). This approach was selected because the radioiodines contribution essentially all of the dose to the infant's thyroid via the cow-milk pathway. The infant's thyroid and the cow-milk pathway are the critical organ and controlling pathway, respectively, for the releases of radioiodine and particulates.

Determination of Ae, (continued)

All other particulates contribute less than 1% of the dose. The effective dose transfer factor is determined by applying equation 3C-1 to the radioiodines. However, in 3C - 1 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS determining the dose, this effective dose transfer factor should be applied to the total release of all radioiodines and to particulates with half lives greater than 8 days.

This uniform application is conservative in providing reasonable assurance that the

-actual dose will not be underestimated by the use of this simplified method.

The determination of Aeff is limited to three years (1978, 1979, and 1980) because of the changes that occurred in the waste processing system. A demineralizer system replaced the previously used evaporator in the liquid waste processing system. Aff was re-evaluated using gas radwaste data from 1992, 1993, and 1994. The re-evaluation indicated that no significant changes have occurred in the radioactive distribution of the release mixture from the Gaseous Radwaste System.

As can be seen from Tables 3C-1 and 3C-2, the effective dose transfer factor varies little from year to year. The maximum observed variability from the average value is 13% for the noble gases and 25% for the radioiodines. This variability is minor considering other areas of uncertainty and conservatism inherent in the environmental dose calculational models.

To provide an additional degree of conservatism, a factor of 0.8 is introduced into the dose calculational process when the effective dose transfer factor is used. This added conservatism provides additional assurance that the evaluation of doses by the use of a single effective factor will not significantly underestimate any actual doses in the environment.

3C - 2 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 3.0 RADIOACTIVE GASEOUS EFFLUENTS Table 3C-1 Effective Dose Transfer Factors: Noble Gases-Air Dose Table 3C-2 Effective Dose Transfer Factor for Air-Grass-Cow-Milk-Infant-Thyroid Pathway, TG 131 Radio nuclide Annual Airborne Fraction Dose Factor" Weighted Dose Factor - TG131 Release (Q) mrem/vr mrem/r 2

(Pe((lCiI(m .sec))

1978 1-131 0.381 0.688 9.9E11 6.9E11 1-133 0.129 0.233 1.3E10 1-135 0.044 0.079 5.2E6 - -

1979 1-131 0.0188 0.520 9.9E11 5.2E11 1-133 0.0156 0.432 1.3E10 1-135 0.0018 0.048 5.2E6 1980 1-131 0.0518 0.756 9.9E11 7.5E11 1-133 0.0124 0.181 1.3E10 1-135 0.0043 0.063 5.2E6 Averageb 6.5E11 a-Air-grass-cow-milk-infant-thyroid dose transfer factor.

b-Effective dose commitment transfer factor is the average of weighted dose transfer factor over three years.

3C- 1 11/22/02

SECTION 4 TOTAL DOSE FROM RADIOACTIVE EFFLUENTS, LIQUID AND GASEOUS

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 40 TOTAL DOSE CONTROL 4.1:LIMITS OF TOTAL DOSE TO MEMBERS OF THE PUBLIC The annual (calendar year) dose or dose commitment to any MEMBER OF THE PUBLIC 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 whole body or any organ, except the thyroid, which shall be limited toless 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 2.3a., 2.3b., 3.3a., 3.3b.,

3.4a., or 3.4b., calculations shall be made including direct radiation contributions from the units to determine whether the above limits of Control 4.1 have been exceeded. If such is the case, prepare and submit to the Commission within 30

.. - - days, pursuant to Control 1.6.6, 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(a)(4), 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 Administrative Control section 1.6.3 are not applicable.

4-1 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 4.0 TOTAL DOSE CONTROL 4.1:LIMITS OF TOTAL DOSE TO MEMBERS OF THE PUBLIC (continued)

SURVEILLANCE REQUIREMENTS 4.1.1. Cumulative dose contributions from liquid and gaseous effluents shall be determined in accordance with Surveillances 2.3, 3.3, and 3.4, and in accordance with the methodology and parameters in this ODCM.

4.1.2. Cumulative dose contributions from direct radiation from the units and the methodology used shall be indicated in the Annual Radioactive Effluent Release Report. This requirement is applicable only under conditions set forth inACTION a. of Control 4.1 METHOD 4.11: LIMITS OF TOTAL DOSE TO MEMBERS OF THE PUBLIC DISCUSSION:

Control 4.1 implements 40 CFR Part 190.l1Oa. It requires the annual (calendar year) dose or dose commitment to any member of the public from all uranium fuel cycle operations to be limited to less than or equal to 75 mrem to the thyroid and 25 mrem to the total body or any other organ.

Fuel cycle sources or nuclear power reactors other than the Turkey Point Plant itself do not measurably or significantly increase the radioactivity concentration in the vicinity of the Plant; therefore, only radiation and radioactivity in the environment attributable to the,--

Plant itself are considered in the assessment of compliance with 40 CFR Part 190.102.

In the event a dose calculated for the purpose of assessing compliance with Control 2.3, 3.3, or 3.4 exceeds 2 times the limit stated therein, then a calculation shall be made to determine whether any limit in Control 4.1 has been exceeded. The total dose calculated pursuant to Control 4.1 must include direct radiation contributions and the methodology for calculating direct radiation contribution must be indicated in the Annual Radioactive Effluent Release Report. These calculations should be made on the basis of radioactive effluents during the year-to-date and reference meteorological data or averaged meteorological data during completed quarters of the year-to-date.

Separately, an evaluation of doses due to effluents during the year is performed annually and reported in the Annual Radioactive Effluent Release Report submitted each year.

This evaluation uses reference meteorological data or annual averaged meteorological data concurrent with the annual gaseous releases to evaluate atmospheric dispersion, deposition, and plume gamma exposure.

4-2 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 4.0 TOTAL DOSE CONTROL 4.1: LIMITS OF TOTAL DOSE TO MEMBERS OF THE PUBLIC (continued)

METHOD 4.1: LIMITS OF TOTAL DOSE TO MEMBERS OF THE PUBLIC, (continued)

DISCUSSION, (continued)

To assess compliance with Control 4.1, evaluations of dose due to liquid and gaseous effluents are calculated as described by the equations for:

o total body dose due to liquid effluent via irradiation by radionuclides deposited on cooling canal shoreline (equation 2.3-1)

-.__- - tota, bodY dose dueto: noblegas gamma radiation (equation 4.1-1) o skin dose due to noble gas beta radiation (equation 4.1-2)

- - - :o total body and maximally exposed organ doses due to gaseous effluents of radioactive 1-131, 1-133, tritium, and radioactive material in particulate form

- having a half-life greater than 8 days (equation 3.4-2).

The doses are calculated on the basis of liquid and gaseous effluents from the Plant,

.7-samprled and analyzed in accordance with ODCM Tables 2.2-1 and 3.2-1.

The receptor of the dose is described such that the dose to any member of the public is lnot ikely tobe underestimated.- The receptor is selected on the basis of the combination of applicable pathways of exposure to gaseous effluent identified in the annual land use

census and maximum ground level X/Q at the residence. Conditions more conservative than appropriate for the maximally exposed person may be assumed in the dose assessment. Environmental pathway-to-dose transfer factors used in the dose calculations appear in Appendix 3B.

When assessing compliance with 40 CFR Part 190 or 10 CFR Part 50 Appendix I dose limits, Radiological Environmental Monitoring Program results may be used to indicate actual radioactivity levels in the environment attributable to the Turkey Point Plant as an alternate to calculating the concentrations from radioactive effluent measurements. The measured environmental activity levels may thus be used to supplement the evaluation of doses to real persons for assessing compliance with 40 CFR Part 190 or 10 CFR Part 50 Appendix I.

4-3 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 4.0 TOTAL DOSE CONTROL 4.1:LIMITS OF TOTAL DOSE TO MEMBERS OF THE PUBLIC (continued)

METHOD 4.1: LIMITS OF TOTAL DOSE TO MEMBERS OF THE PUBLIC, (continued)

DOSE TO A PERSON FROM NOBLE GASES Control 4.1 requires the calculation of the annual (calendar year) dose or dose commitment to a member of the public exposed to radioactive liquid and gaseous effluents from the plant. One component of personal dose is total body irradiation by gamma rays from noble gases. Another is irradiation of skin by beta and gamma radiation from noble gases. The methods for calculating these doses are presented

- - below.-

The amount of radioactive noble gas discharged is determined in the manner described in Method 3.2.

-- GAMMA DOSE TO TOTAL BODY

--The gamma radiation dose to the whole body of a member of the public as a consequence of noble gas released from the Plant is calculated with the equation:

. .. "" :*..'i:.D7= Q ZiQi- Pýi_ Eqn 4.1-1 whre:

D7 = noble gas gamma dose to total body, (mrem)

.Q = quantity of radioactive noble gas i discharged in gaseous effluent, (pCi) x/Q = atmospheric dispersion factor at the off-site location of interest, (sec/m 3)

Pyi = factor converting time integrated, ground level concentration of noble gas nuclide, I, to total body dose from gamma radiation listed in Table 4.1-1, mrem (jtCi-sec/m 3) 4-4 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 4.0 TOTAL DOSE CONTROL 4.1:LIMITS OF TOTAL DOSE TO MEMBERS OF THE PUBLIC, (continued)

METHOD 4.1: LIMITS OF TOTAL DOSE TO MEMBERS OF THE PUBLIC, (continued)

DOSE TO A PERSON FROM NOBLE GASES, (continued)

When the total body dose due to gamma radiation from noble gas required by Control 4.1 is calculated, the most exposed receptor is located 1.75 miles west northwest of the plant where the reference meteorological dispersion factor, X/Q, is 2.75 x 10-7 sec/m 3 .

This calculation is the same technique used in Control 3.2, Equation 3.2-1, but is -

extrapolated to an annual release and the x/Q value is for the most exposed receptor, not the minimum dispersion point off-site.

DOSE TO SKIN The radiation dose to the skin of a member of the public due to noble gas released from the Plant may be calculated with the equation*

D [ zQi*S/+J.Jx !boA] Eqn.4"l-2 where:..

D =dose to skin due to noble g~ases (rrem)

X/a .-= atmospheric dispersion factor at the off-site location of interest, (sec/M3). -

Qj = quantity of radioactive noble gas i discharged in gaseous effluent, (jtCi).

Spi = factor converting time integrated ground level concentration of noble gas to skin dose from beta radiation listed in Table 4.1-1, mrem (pCi-sec/m3 )

1.11 = ratio of tissue dose equivalent to air dose in a radiation field, (mrem/mrad)

Ayj = factor for converting time integrated, ground-level concentration of noble gas radionuclide i to air dose from its gamma radiation listed in Table 4.1-2, mrad (pCi-sec/m 3).

4-5 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 4.0 TOTAL DOSE CONTROL 4.1:LIMITS OF TOTAL DOSE TO MEMBERS OF THE PUBLIC, (continued)

METHOD 4.1: LIMITS OF TOTAL DOSE TO MEMBERS OF THE PUBLIC, (continued)

DOSE TO A PERSON FROM NOBLE GASES, (continued)

When the skin beta dose due to noble gas required by Control 4.1 is calculated, the most exposed receptor is located 1.75 miles west northwest of the Plant where the reference meteorological dispersion factor, X/Q, is 2.75 x 10-7 sec/m 3 .

The total dose to the skin from noble gases is approximately equal to the beta radiation dose to the skin plus the gamma radiation dose to the total body.

This is the same technique used in Control 3.2, Equation 3.2-3, but is extrapolated to an annual release, and the X/Q value is for the most exposed receptor rather than the minimum dispersion point off-site.

DOSE.TO A PERSON DUE TO DIRECT RADIATION When the dose due to direct radiation required by Control 4.1 is required to be calculated, the most appropriate TLD reading from the Radioactive Environmental Monitoring Program shall be used. This TLD reading shall be summed with the dose to a person from noble gas to obtain the total dose to Members of the Public. Specific methodology and which TLD measurement(s) used shall be described in the Annual Radioactive Effluent Release Report.

4-6 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 4.0 TOTAL DOSE CONTROL 4.1:LIMITS OF TOTAL DOSE TO MEMBERS OF THE PUBLIC (continued)

METHOD 4.1: LIMITS OF TOTAL DOSE TO MEMBERS OF THE PUBLIC, (continued)

.BASIS 4.11: LIMITS OF TOTAL DOSE TO MEMBERS OF THE PUBLIC This control is provided to meet the dose limitations of 40 CFR Part 190 that have been incorporated into 10 CFR 20.1301(d). The control requires the preparation and submittal of a Special Report whenever the calculated doses due to releases of radioactivity and to radiation from uranium fuel cycle sources exceed 25 mrems to the whole body or any organ, except the thyroid, which shall be limited to less than or equal to 75 mrems. For sites containing up to four 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 units 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 purposes of the Special Report, it may be assumed that the dose commitment to the MEMBER of the PUBLIC from other 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 the requirements 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 190.11 and 10 CFR 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 2.2 and 3.2. 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.

4-7 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 4.0 TOTAL DOSE CONTROL 4.1:LIMITS OF TOTAL DOSE TO MEMBERS OF THE PUBLIC (continued)

METHOD 4.1: LIMITS OF TOTAL DOSE TO MEMBERS OF THE PUBLIC, (continued)

Table 4.1-1 Transfer Factors for Maximum Dose to a Person Offsite due to Radioactive Noble Gases Air Dose Transfer Factors Pyi S3i -

S - mrem mrem Radionuclide 4Ci sec/m3 ) (RCi sec/mr3 )

Kr-83m 2.4 E-9 Kr-85m 3.7 E-5 4.6 E-5.

4.2 E-5 Kr-85 5.1 E-7 Kr-87 1.9 E-4 Kr-88 4.7 E-4 .

3.2 E-4 Kr-89 5.3 E-4 Kr-90 4.9 E-4 Xe-131m 2.9 E-6 1.5 E-E75 Xe-1 33m 8.0 E-6 3.1 E-E 9 .'7 E -6 . . . .. ...... .. .....

Xe-133 9.3 E-6 Xe-1 35m 9.9 E-5 2.3 E-,

5.9 E-5 i - -

Xe-135 5.7 E-5 3.9 E-4 Xe-1 37 4.5 E-5 1.3 E-4 Xe-138 2.8 E-4 8.5 E-5 Ar-41 2.8 E-4 Ref: Regulatory Guide 1.109, Revision 1, Table B-1.

Note: Values in the regulatory guide are quoted in units of pCi yr, to convert to units of pCi sec multiply by a factor of 3.171 E-2.

4-8 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 4.0 TOTAL DOSE CONTROL 4.1: LIMITS OF TOTAL DOSE TO MEMBERS OF THE PUBLIC (continued)

METHOD 4.1: LIMITS OF TOTAL DOSE TO MEMBERS OF THE PUBLIC, (continued)

Table 4.1-2 Transfer Factors for Maximum Offsite Air Dose Air Dose Transfer Factors Ayi Apii mrad mrad Radionuclide (LtCi sec/m 3) (iiCi sec/m 3)

Kr-83m 6.1 E-7 9.1 E-6 Kr-85m 3.9 E-5 6.2 E-5 Kr-85 5.4 E-7 6.2 E-5 Kr-87 2.0 E-4 3.3 E-4 Kr-88 4.8 E-4 9.3 E-5 Kr-89 5.5 E-4 3.4 E-4 Kr-90 5.2 E-4 2.5 E-4 Xe-1 31 m 4.9 E-6 3.5 E-5 Xe-1 33m 1.0 E-5 4 .7 E-5 Xe-133 1.1 E-5 3.3 E-5 Xe-1 35m 1.1 E-4 2.3 E-5 Xe-1 35 6.1 E-5 7.8 E-5 Xe-137 4.8 E-5 4.0 E-4 Xe-1 38 2.9 E-4 1.5 E-4 Ar-41 2.9 E-4 1.0 E-4 Ref: Regulatory Guide 1.109, Revision 1, Table B-1 Note: Values in the regulatory guide are in units of pCi*yr, to convert to units of .tCi*sec multiply by a factor of 3.171 E-2.

4-9 11/22/02

SECTION 5 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM CONTROL 5.1: CONDUCT OF SAMPLING AND ANALYSIS The Radiological Environmental Monitoring Program shall be conducted as specified.in Table 5.11-1.

APPLICABILITY: At all times.

ACTION:

a. With the Radiological Environmental Monitoring Program not being conducted as specified in Table 5.1-1, prepare and submit to the Commission, in the Annual Radiological Environmental Operating Report required by Control 1.4, a description of the reasons for not conducting the program as required and the plans for preventing a recurrence.

b, With the level of confirmed ** radioactivity as the result of plant effluents in an environmental sampling medium at a specified location exceeding the reporting levels of Table 5.1-2 when averaged over any calendar quarter, prepare and submit to the Commission within 30 days, pursuant to Control 1.6.6, 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 2.3, 3.3, or 3.4. When more than one of the radionuclides in Table 5.1-2 are detected in the sampling medium, this report shall be submitted if:

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

When radionuclides other than those in Table 5.1-2 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 Control 2.3, 3.3, or 3.4. 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 required by Control 1.4

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

- A confirmatory reanalysis of the original, a duplicate, or a new sample may be desirable, as appropriate. The results of the confirmatory analysis shall be completed at the earliest time consistent with the analysis, but in any case within 30 days.

5-1 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM CONTROL 5.11: CONDUCT OF SAMPLING AND ANALYSIS (continued)

ACTION (continued)

c. With milk or broad leaf vegetation samples unavailable from one or more of the sample locations required by Table 5.1-1, identify specific locations for obtaining replacement samples and add them within 30 days to the Radiological Environmental Monitoring Program given in this ODCM. The specific locations from which samples were unavailable may then be deleted from the monitoring program.

Pursuant to Control 1.3, submit in the next Annual Radioactive Effluent Release Report documentation for a change in the ODCM including a revised figure(s) and table for this ODCM reflecting the new location(s) with supporting information identifying the cause of the unavailability of samples and justifying the selection of the new location(s) for obtaining samples.

d. The provisions of Administrative Control section 1.6.3 are not applicable.

SURVEILLANCE REQUIREMENTS 5,1.1 The radiological environmental monitoring samples shall be collected pursuant to Table 5.1-1 from the specific locations given in the table and figure(s) in this ODCM, and shall be analyzed pursuant to the requirements of Table 5.1-1 and the detection capabilities required by Table 5.1-3.

5-2 11/22/02

TURKEY POINT UNIT3i &4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM CONTROL 5.1 : CONDUCT OF SAMPLING AND ANALYSIS,"(c0ntinUed)

TABLE 5.1-1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAMW)

EXPOSURE NUMBER OF REPRESENTATIVE SAMPLING AND TYPE AND FREQUENCY OF ANALYSIS(4 )

PATHWAY AND/OR SAMPLES AND SAMPLE 'COLLECTION SAMPLE LOCATIONS(2 )(3 ) FREQUENCY(4)

1. Direct Radiation(5) 21 Monitoring Locations Continuous Monitoring with Gamma Exposure Rate - quarterly Sample Collection Quarterly(6)

2. Airborne Five Locations Continuous Sampler Radioiodine Filter- Analysis for 1-131 weekly Radioiodine and Operation with sample Particulate filter - Gross beta radioactivity analysis _

Particulates collection at least weekly or 24 hours2.777778e-4 days 0.00667 hours 3.968254e-5 weeks 9.132e-6 months following filter change(7 ); ; Gamma isotopic more frequently if required by analysis(8 ) of composite(7 ) (by location) quarterly.

dust loading

3. Waterborne(1°)

a. Surface(8 ) Three Locations(9 ) Monthly Gamma isotopic(8) and tritium analysis monthly.

b. Sediment from Three Locations Semiannually Gamma isotopic analysis(8 ) semiannually.

Shoreline

4. Ingestion

a. Fish and Invertibrates

1. Crustacea Two Locations Semiannually Gamma isotopic analysis(8 ) semiannually.

2. Fish Two Locations Semiannually Gamma isotopic analysis(8 ) semiannually.

b. Food Products

1. Broad Leaf Three Locations (11) Monthly when available Gamma isotopic analysis (8)and 1-131 analysis Vegitation monthly.

5-3 12/23/03

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM CONTROL 5.1: CONDUCT OF SAMPLING AND ANALYSIS (continued)

TABLE NOTATIONS - TABLE 5.1-1 (Continued)

(1) Deviations are permitted from the required sampling schedule if specimens are unobtainable due to circumstances such as hazardous conditions, seasonal unavailability, and malfunction of automatic sampling equipment or other legitimate reasons. If specimens are unobtainable due to sampling equipment malfunction, corrective action shall be taken 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 1.4 (2) Specific parameters of distance and direction sector from the centerline of the plant vent stack and additional description where pertinent, shall be provided for each and every sample location in Table 5.1-1 in a table and figure(s) in this ODCM.

(3) 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 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 given in this ODCM.

(4) The following definition of frequencies shall apply to Table 5.1-1 only:

Weekly - Not less than once per calendar week. A maximum interval of 11 days is allowed between the collection of any two consecutive samples.

Semi-Monthly - Not less than 2 times per calendar month with an interval of not less than 7 days between sample collections. A maximum interval of 24 days is allowed between collection of any two consecutive samples.

Monthly - Not less than once per calendar month with an interval of not less than 10 days between collection of any two consecutive samples.

Quarterly - Not less than once per calendar quarter.

Semiannually - One sample each between calendar dates (January 1 - June 30) and (July 1 - December 31). An interval of not less than 30 days will be provided between sample collections.

The frequency of analyses is to be consistent with the sample collection frequency.

5-4 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM CONTROL 5.1: CONDUCT OF SAMPLING AND ANALYSIS (continued)

TABLE NOTATIONS - TABLE 5.1-1 (continued)

(5) One 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 purposes 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 (6) Refers to normal collection frequency. More frequent sample collection is permitted when conditions warrant it.

(7) Airborne particulate sample filters are 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. In addition to the requirement for a gamma isotopic on a composite sample, a gamma isotopic is also required for each sample having a gross beta radioactivity

- which is > 1.0 pCi/m 3 and which is also > 10 times that of the most recent control sample.

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

(9 Off-shore' grb samples> --

(10) Discharges from the Turkey Point Plant do not influence drinking water or ground water pathways.

(11) Samples of broad leaf vegetation grown nearest each of two different offsite locations of highest predicted annual average ground level D/Q, and one sample of similar broad leaf vegetation at an available location 15-30 km distant in the least prevalent wind direction based upon historical data in this ODCM.

5-5 12/23/03

TURKEY.POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL EI' NVIRONMENTAL MONITORING PROGRAM "

CONTROL 5.1: CONDUCT OF SAMPLING AND ANALYSIS (continued)

TABLE 5.1-2 REPORTING LEVELS FOR RADIOACTIVITY CONCENTRATIONS IN ENVIRONMENTAL SAMPLES ANALYSIS WATER AIRBORNE FISH MILK FOOD PRODUCTS PARTICULATE,,' , I (pCi/I) PR CULATE (pCi/kg, wet) (pCi/I) (p1Ci/kg, wet)

OR GASES (pCi/r 3)

H-3 30,000 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 Cs-1 37 50 20 2,000 70 2,000 Ba-La-140 200 300 Since no drinking water pathway exists, a value of 30,000 pCi/I is used. For drinking water samples a value of 20,000 pCi/I is used.

This is a 40 CFR 141.16 Table A value. I

- Applies to drinking water

- - An equilibrium mixture of the parent and daughter isotopes which corresponds to the reporfing value of the parent isotope 5-6 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM CONTROL 5.1 " CONDUCT OF SAMPLING AND ANALYSIS (continued)

TABLE 5.1-3 DETECTION CAPABILITIES FOR ENVIRONMENTAL SAMPLE ANALYSIS(1 )

LOWER LIMIT OF DETECTION (LLD) (2)(3)

ANALYSIS WATER AIRBORNE PARTICULATE FISH SEDIMENT MILK FOOD PRODUCTS (pCi/I) OR GASES (pCi/m 3) (pCi/kg, wet) (pCi/kg, dry) (pCi/I) (pCi/kg, wet)

Gross Beta 4 0.01 H-3 3,000 Mn-54 15 130 Fe-59 30 260 Co-58 15 130 Co-60 15 130 Zn-65 30 260 Zr-Nb-95 15(5) 1-131 1(4) 0.07 .1 60 Cs-134 15 0.05 130 -150 015 60 Cs-137 18 0.06 . 150 180 18 80 Ba-La-140 15(5) 15(5)

Since no drinking water pathway exists, a value of 3,000 pCi/I is used. For drinking water samples a value of 2,(000 pCi/I is used. Source NUREG-0472, Rev. 3.

An equilibrium mixture of the parent and daughter isotopes 'ýwhich corresponds' to the reporting value of the parent isotope 5-7 12/23/03

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM CONTROL 5.1: CONDUCT OF SAMPLING AND ANALYSIS (continued)

TABLE NOTATIONS - TABLE 5.1-3 (Continued)

(1) This 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 1.4.

(2) Required detection capabilities for thermoluminescent dosimeters used for environmental measurements are given in Regulatory Guide 4.13.

(3): -The LLD is definedfor p-irposes of these controls; -asthe 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 (S*b E

V- 2.22. Y [exp(-XAt)]

Where:

LLD = the "a priori" lower limit of detection as defined above as picoCuries per unit mass or volume, Sb = the standard deviation of the background counting rate or of the counting rate of a blank sample as appropriate (counts per minute),

E = the counting efficiency (counts per disintegration),

V = the sample size (units of mass or volume),

2.22 = the number of disintegrations per minute per picoCurie, Y = the fractional radiochemical yield, when applicable, X = the radioactive decay constant for the particular radionuclide At = the elapsed time between environmental collection, or end of the sample collection period, and time of counting (sec).

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

5-8 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM CONTROL 5.1" CONDUCT OF SAMPLING AND ANALYSIS (continued)

TABLE NOTATIONS (continued) - TABLE 5.1-3 (continued)

(3) The LLD is defined (continued)

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. 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 1.4.

(4) LLD for drinking water. If no drinking water pathway exists, a value of 15pCi/I may be used.

(5) An equilibrium mixture of the parent and daughter isotopes which corresponds to 15 pCi/I of the parent isotope.

METHOD 5.1: RADIOLOGICAL ENVIRONMENTAL SURVEILLANCE - TURKEY POINT PLANT It is the policy of Florida Power and Light Company (FPL) that the Turkey Point 3 and 4, Radiological Environmental Monitoring Programs, (REMP), are conducted by the State of Florida Department of Health (DOH), pursuant to an Agreement between FPL and DOH. The policy also states that the coordination of the REMP with DOH and compliance with the REMP requirements are the responsibility of the Nuclear Division Health Physics/Chemistry Staff.

The following pages describe the actual sampling and analysis program implemented to satisfy ODCM Table 5.1-1.

5-9 6/4/07

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM CONTROL 5.1: CONDUCT OF SAMPLING AND ANALYSIS (continued)

RADIOLOGICAL ENVIRONMENTAL SURVEILLANCE Key to Sample Locations Pathway Location Description Samples Sample Approx. Direction Collected Collection Distance Sector Frequency (miles)

Direct N-2 Convoy TLD Quarterly 2 N Radiation Point Direct N-7 Black Point Marina parking TLD Quarterly 7 N Radiation lot on siren pole Direct N-1 0 Old Cutler Rd across from TLD Quarterly 10 N Radiation Perdue Med. Ctr. on siren pole.

Direct NNW-2 East end of N. Canal Dr. on TLD Quarterly 2 NNW Radiation siren pole E. of 117th Ave.

Direct NNW-10 Bailes Rd. E. of US 1 on TLD Quarterly 10 NNW Radiation siren pole.

Direct NW-1 Turkey Point TLD Quarterly 1 NW Radiation Entrance Rd Direct NW-5 Intersection of Mowry Dr. & TLD Quarterly 5 NW Radiation 117th Ave. on siren pole. " 4 1 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM CONTROL 5.1 : CONDUCT OF SAMPLING AND ANALYSIS (continued)

RADIOLOGICAL ENVIRONMENTAL SURVEILLANCE Key to Sample Locations Pathway Location Description Samples Sample Approx. Direction Collected Collection Distance Sector Frequency (miles)

Direct NW-10 On Newtown Rd. N. of TLD Quarterly 10 NW Radiation Coconut Palm Drive on siren pole.

Direct W-5 Palm Drive 0.3 mi. west of TLD Quarterly 5 W Radiation Tallahassee Rd.

Direct WNW-10 NW 2nd Ave. S. of Campbell TLD Quarterly 10 WNW Radiation Dr. at Hmstd. Middle School on siren pole.

Direct W-1 On site north side of TLD Quarterly 1 W Radiation Discharge Canal.

Direct W-9 Card Sound Rd. 0.6 mi. SSE TLD Quarterly 9 W Radiation of US 1 on siren pole. _ _ _ _ _ _

Direct WSW-8 Card Sound Rd. 3.4 mi. SSE%, TLD Quarterly 8 WSW Radiation of US 1 on siren pole. _, -

Direct SW-1 On site near land TLD Quarterly 1 SW Radiation utilization offices 5-11 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM CONTROL 5.1: CONDUCT OF SAMPLING AND ANALYSIS (continued)

RADIOLOGICAL ENVIRONMENTAL SURVEILLANCE Key to Sample Locations Pathway Location Description Samples Sample Approx. Direction Collected Collection Distance Sector Frequency (miles)

Direct SSE-1 On site South East side of TLD Quarterly SSE Radiation cooling canals at "Turtle Tr Point" Direct SW-8 Card Sound Rd. 5 mi. SSE TLD Quarterly 8 SW Radiation of US I at entrance to Navy facility.

Direct SSW-5 On site, southwest corner TLD Quarterly 5 SSW Radiation of cooling canals Direct SSW-10 At Card Sound TLD Quarterly 10 SSW Radiation Bridge on siren pole.

Direct S-5 On site, south east end of TLD Quarterly 5 5 Radiation cooling canals.

Direct S-10 Card Sound Road at TLD Quarterly 10 5 Radiation Steamboat Creek.

CONTROL 5.1: CONDUCT OF SAMPLING AND ANALYSIS (continued)

RADIOLOGICAL ENVIRONMENTAL SURVEILLANCE Key to Sample Locations 5-12 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Radiation Direct Radiation NNE-22* Natoma Substation TLD Quarterly 22 NNE Airborne T5.1 Entrance to Homestead Radioiodine Weekly 2 NNW Bayfront Park and Particulate Airborne T71 Red Barn / Beach Area Radioiodine Weekly 0.5 NNE (Alternate to T51) and Particulate Airborne T57 Siren pole 27, intersection of Radioiodine Weekly 4 NW SW 112th Ave and SW 304th and St. Particulate Airborne T52 Florida City Radioiodine Weekly 7 W (Alternate to Substation and T57) Particulate Airborne T58 Turkey Point Radioiodine Weekly 1 NW Entrance Rd and Particulate

Denotes control sample

, 5-13 11/22/02

TURKEY POINT UNIT 3 &4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL' MONITORING 5,GCEPROGRAM CONTROL 5.1 : CONDUCT OF SAMPLING AND ANALYSIS (continued)

RADIOLOGICAL ENVIRONMENTAL SURVEILLANCE Key to Sample Locations ,

Pathway Location Description Samples Sample Approx. Direction Collected Collection Distance Sector Frequency (miles)

Airborne T64* Natoma Substation Radioiodine Weekly 22 NNE and Particulate Airborne T72 Turkey Point Land Utilization Radioiodine Weekly <1 WSW Entrance and Particulate Waterborne T42 Biscayne Bay, at Turkey Point Surface Water Monthly <1 ENE Shoreline Semi-V Sediment annually Waterborne T67* Biscayne Bay, vicinity of Cutler Surface Water Monthly 13-18 N,NNE Plant north to Matheson Hammock Park Shoreline Semi-Sediment annually Waterborne T81 Card Sound, near mouth of old Surface Water Monthl6 Motl6 SufcWae discharge canal Shoreline Semi-Sediment annually Denotes control sample.

5-14 11/22/02

TURKEY POINT UNIT 3 &,4OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING"PROGRAM CONTROL 5.1: CONDUCT OF SAMPLING AND ANALYSIS (continued)

RADIOLOGICAL ENVIRONMENTAL SURVEILLANCE Key to.Sample Locations Pathway Location Description S pe Sample Approx. Direction Collected Collection Distance Sector Frequency (miles)

Food T67" Biscayne Bay, vicinity of i Crustacea . Semi- iF", 13-18 N,NNE Products Cutler PlantHammock Matheson north to Park , annually an n u"l .

Fish- '".. . Semi-annually Food T81 Card Sound near mouth of Crustacea Semi- 6 S Products old Discharge Canal. annually Fish Semi-annually Food T40 South of Palm Dr. on SW Broad Monthly 3 W/WNW Products 117th St extension leaf vegetation Food Products T41 Palm Dr. West of FPL Broad Monthly 2 WNW wellness center near the site leaf boundary vegetation Food Products T67* Near Biscayne Bay, Vicinity Broad Monthly 13 - 18 N, NNE of Cutler Plant North to leaf Matheson Hammock Park vegetation

Denotes control sample.

5-15 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM CONTROL 5.11: CONDUCT OF SAMPLING AND ANALYSIS (continued)

BASES 5.1 : 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 exposure of MEMBERS OF THE PUBLIC resulting from the plant 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 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.

The required detection capabilities for environmental sample analyses are tabulated in terms of the lower limits of detection (LLDs). The LLDs required by Table 5.1-3 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 Currie, L. A., "Lower Limit of Detection: Definition and Elaboration of a Proposed Position for Radiological Effluent and Environmental Measurements," NUREG/CR-4007 (September 1984), in HASL

. - Procedures Manual, HASL-300 and Hartwell, J. K. "Detection Limits for Radioanalytical Counting Techniques," Atlantic Richfield Hanford Company Report ARH-SA-215 (June 1975).

5-16 12/23/03

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM NEAR SITE SAMPLING LOCATIONS Figure 5.1-1 BJSCAYNE."`

Floridacity -T7-41 My w-i 1-42 X

~~~. ... w~1 (S2 5-17....

12/23/03

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM DISTANT REMP SAMPLING LOCATIONS Figure 5.1-2 errie T-67 NNE-22 & T-64 South Man-dHi*giCu..er Ridge 22 mUiloff map N-1

-:: ~ ~~

... ....... ~ ~ ~ ~ ~

.. =:==.;

~ ~ .... .. ....

... :::-: M Doc~ye~

/ l ... ................... ..... ..............

N-7. ....

Sinds Key N-5 Jomestea.......

w-*

.::,. *:: * . :... ).:,.:i - .:- .:.=.:. ... *.........:::::::::::::::::::::

IPTN S. Od: R.1'ds- Key Turte H.rbr Channel'

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iiiiiiii~~iiiiiiii i~iiiiiiii~iii~iiiiiiiiiiiiiiiiii

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. .. . ..... ... ... ........ ....... . i *- '¢ j:: r~b' , "4 4;Jr ;;; . ;; JJJ . "...,' ........... r';; ..

NNE-22 and T-o64 are 22 miles from Tur ey Point and outside the map area 5-18 12/23/03

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM CONTROL 5.2 LAND USE CENSUS A Land Use Census shall be conducted and shall identify within a distance of 8 km (5 miles) the location, in each of the 16 meteorological sectors, of the nearest milk animal, the nearest residence, and the nearest gardens* of greater than 50 m 2 (500 ft2) producing broad leaf vegetation.

APPLICABILITY: At all times.

ACTION:

a. With a Land Use Census identifying a location(s) that yields a calculated dose or dose commitment greater than the values currently being calculated in Control 3.4, pursuant to Control 1.3, identify the new location(s) in the next Annual Radioactive Effluent Release Report.

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 5.1, add the new location(s) within 30 days to the Radiological Environmental Monitoring Program given in this ODCM. 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 1.3, submit in the next Annual Radioactive Effluent ReleaselReport documentation f.o6r.a*

change to this ODCM including a revised figure(s) and table(s) for the ODCM --

reflecting the new location(s) with information supporting the change in sampling locations.

c. The provisions of Administrative Control section 1.6.3 are not applicable.

Broad leaf vegetation sampling 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. Specifications for broad leaf vegetation sampling in Table 5.1-1, Part 4.b., shall be followed, including analysis of control samples.

5-19 12/23/03

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SURVEILLANCE REQUIREMENTS 5.2.1 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, 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 1.4 BASIS 5.2: 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 or from consulting with local agricultural authorities shall be used. This census satisfies the requirements of Section IV.B.3 of Appendix I to 10 CIFR Part 50. Restricting the census to gardens of greater than 50 M2 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/m2.

5-20 12/23/03

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM CONTROL 5.3: INTERLABORATORY COMPARISON PROGRAM Analyses shall be performed on all samples, supplied as part of an Interlaboratory Comparison Program, that correspond to the matrices shown on Table 5.3-1 This control may be satisfied by participation in a government sponsored radiological measurements Intercomparison program that involves at least three of the matrices shown in Table 5.3-1 APPLICABILITY: At all times.

ACTION:

a. With analysis not being performed as required above, report the corrective actions taken to prevent recurrence to the Commission in the Annual Radiological Environmental Operating Report pursuant to Control 1.4.

b. The provisions of Control 1.6.3 are not applicable.

SURVEILLANCE REQUIREMENTS:

5.3.1 A summary of the results obtained, as part of the above required Interlaboratory Comparison Program shall be included in the Annual Radiological Environmental Operating Report pursuant to Control 1.4.

METHOD 5.3:

5.3.1 The Program shall be conducted such that on an annual basis:

At least three of the matrices will be involved, and at least two of the analytical methods will be evaluated, and for Gamma Spectroscopy, a majority of the nuclides shown in Table 5.3-1 will be included.

5.3.2 Any laboratory approved by FP&L may provide samples for the Intercomparison Program provided that the radioisotopes used for sample preparation are traceable to the National Institute of Standards and Technology (NIST).

5-21 12/23/03

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM METHOD 5.3: (continued) 5.3.3 Analysis of Matrix samples shall be capable of achieving ODCM Table 5.1-3 prescribed Lower Limit of Detection (LLD) on a blank sample.

5.3.4 Results within 20% of expected should be considered acceptable. Results exceeding 20% but within 35% require a description of probable cause and actions performed to bring the analysis into conformance. Results exceeding 35% are considered Not Acceptable; the Matrix shall be replaced and reanalyzed.

BASIS 5.3: INTERLABORATORY COMPARISON PROGRAM - -

The requirement for participation in an approved Interlaboratory Comparison Program is provided to ensure that independent checks on the precision and accuracy of the measurements of radioactive materials 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 /1to.

10 CFR 50.

The Interlaboratory Comparison Program described herein provides an independent check on the precision and accuracy of the radiological monitoring measurements .. - .

conducted as part of the Radiological Environmental Monitoring Program. The purpose of the Interlaboratory Comparison Program described in this appendix is16toprovide -ý*- --

adequate confidence in the results of Turkey Point's radiological monitoring measurements, by providing an independent test of the ability to measure radionuclides in the sample medium.

5-22 12/23/03

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM TABLE 5.3-1 INTERLABORATORY COMPARISON PROGRAM SAMPLE ANALYSIS (1)

Analytical [ANALYSIS WATER c' AIRBORNE PARTICULATE OR SOIL VEGETATION Method (2) GASES I GB Gross Beta X H3 H-3 X Co-57 X Co-60 X X X Cs-134 X X Cs-137 X X X X Ce-144 X GS Mn-54 X K-40 X X Ru-106 X

_Sb-125 .,_X I I A )

U

!*i '

5-23 12/23/03

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM TABLE NOTATIONS

1. The sample matrices shown on table 5.3-1 correspond to the matrices shown in Tables 5.1-1 & 5.1-2, with the following exceptions:

a. Milk is not currently in the REMP sampling program; there are no milk animals in the area encompassed by the Land Use Census. Therefore, inclusion of milk samples in the Interlaboratory Comparison Program is not required. Continued exclusion of milk in the Interlaboratory Comparison Program is acceptable until

-. the Land Use Census indicates the existence of milk producing animals within the geographic area covered by REMP; see note 3, below.

b. The INGESTION exposure pathway is represented by inclusion of Broad Leaf Vegetation in the Interlaboratory Comparison Program cross checks. Fish and Invertebrate samples are not included in the cross check program due to the instability of maintaining radioactivity in a fixed matrix due to decaying tissue and refrigeration limitations.

2 --.T....

he analytical methods to be evaluated are those applied in the current REMP:

a GB - Gross Beta analysis of an Air Filter matrix b* H3 - Tritium in water, using method employed in REMP

c. GS - Gamma Spectroscopy, Quantitative.

3. The Gamma Spectroscopy method for water will suffice for Gamma Spectroscopy of Milk, should milk samples become available. Milk is over 98 % water.

5-24 12/23/03

Turkey Point Supplemental Radiological Environmental Monitoring Program Appendix 5A

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Turkey Point Supplemental REMP Sampling The sampling and analysis program outlined in this appendix is performed in addition to the sample and analysis program required by Control 5.1. The sample sites, frequency, and analyses have been agreed upon by the State of Florida Department of Health and Florida Power and Light Co. These samples are not required to be performed, but based on this agreement, are performed to provide a broader data base for the Radiological Environmental Monitoring Program.

5A- 1 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Turkey Point Supplemental REMP Sampling Pathway: Direct Exposure via TLD Sampling and Collection Frequency: Continuous monitoring with sample collection and analysis performed quarterly.

Name # Description NNW- 6 Siren S29 pole, NE comer Moody Dr. (SW 268 St) &Allapattah (SW 112 Av)

NW- 7 Siren S28 pole, E side Pine Island Rd (SW 132 Av) & N of Waldin Dr (SW280 St.)

NW- 8 Siren" S7 pole, SW 152 Avat E end of SW 248 St WNW- 2 FPL Satellite School, cement pole in school yard WNW- 3 Siren S21 pole, NW corner Palm Dr and Allapattah Rd (SW 117 Av)

WNW-6 Siren S25 pole, W side Tallahassee Rd (SW 137 Av), N of Moody Dr W-8 -Florida City Substation ENE - 1 E end of Turkey Point', past Ranger Station T71 on site "Red Barn" picnic area T72 on site, just outside LU entrance

name = bearing - approx range, miles Pathway: Airborne Radioiodines and particulates Sampling and Collection Frequency: Continuous monitoring with sample collection and analysis performed weekly.

Name Sector Distance Description T41 WNW 2 FPL Satellite School, cement pole in school yard T52 W 8 Florida City Substation T56 N 7 SW comer parking lot @ Black Point Marina 171 NNE 0.5 on site "Red Barn" picnic area

Approximate Distance from plant in miles 5A - 2 11/22/02

TURKEY POINT UNIT 3 & 4 OFFSITE DOSE CALCULATION MANUAL 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM Turkey Point Supplemental REMP Sampling Pathway: Waterborne, Surface Water Sampling and Collection Frequency: Monthly Name Sector Distance Description 175 NW 1.2 Florida City Canal (- cross-street from satellite school)

T84 WSW 0.5 Cooling canal, discharge, - by bridge to parking lot T97 E 0.2 Cooling Canal, intake, - Air Force school area T08 S 5.5 Southern shore of canal system, west of Grand Canal Bridge Approximate Distance from plant in miles Pathway: Waterborne, Vegetation Sampling and Collection Frequency: Quarterly Name Description T84 'Seaweed' from any location in the cooling canal Pathway: Waterborne, Sediment Sampling and Collection Frequency: A = Annual S = Semiannual (All Locations are the Cooling Canals)

Name SCF Description T01 A - Air Force school area T02 A West side of dam @ 'old intake' T03 A North end of collector canals, west of 'Grand Canal' T04 A In front (east) of LU offices T05 / T84 S Cooling canal, discharge, - by bridge to parking lot T06 / T85 S NW corner of canal system T07 A SW comer of canal system T08 A South end of main canal, near bridge T09 A 'Old Discharge Canal' at bend south of earth dam T10 A SE comer of canal system 5A - 3 6/4/07

Turkey Point Supplemental REMP Sampling' Pathway: Ingestion, Milk Sampling and Collection Frequency: Semiannual collection and Gamma-Spec analysis Name Sector Distance Description T99 WNW 12 18 3 rd block of SW 2 6 2 nd St.

(alt) W 10 134th block of SW 2 24 th St.

Pathway: Ingestion, Fish Sampling and Collection Frequency: semi-annual collection and Gamma-Spec analysis . - - .

Name

Sector Distance Description T84 ...--- Cooling Canal Pathway: Ingestion, Food Crop .

Sampling and Collection Frequency: Annual collection (@ harvest) and Gamma-Spec analysis - -

[Description

[INam T43 Sector N thru NW to W Distance*

Various locations:

typically 2 to 10 miles VaridouSlocations : 'truck farm' p6int of Sal-growing fields, miscellaneous other sources of locally grown food crops (e.g., corn, potato, sugar cane, greens, from plant etc)

Although the Name remains the same, the locations can vary with sample availability.

Approximate Distance from plant in miles.

5A-4 11/22/02

Turkey Point Groundwater Sampling Program to Support the INDUSTRY INITIATIVE on Groundwater Protection Appendix 5B 6/4/07

The following sampling and analysis program is performed to meet the INDUSTRY INITIATIVE on Groundwater Sampling. The sample points are the minimum recommended and other points may be sampled in addition. The following notes apply:

1. The sample locations apply after January 1, 2007.

2. All sample results taken in support of the INDUSTRY INITIATIVE (NP-922) for the previous calendar year and required to be included in the Annual Radiological Environmental Operating Report (AREOR) to the NRC due May 1 st shall be reported to the Radiological Environmental Monitoring Program Specialist, Juno Nuclear Operations Support for inclusion in the AREOR.

3. All sample results taken in support of the INDUSTRY INITATIVE (NP-922) for

.- -the previous calendar year and required to be included in the: Annual Radiological Effluent Release Report to the NRC shall be provided to the Chemistry Department for inclusion in the Annual Radioactive Effluent Release Report due April 1 st.

4. No drinking water pathway exists from groundwater at Turkey Point. Since on-site groundwater at Turkey Point Nuclear Plant does not provide a path to drinking water, the criterion in Section 2.2 of the INDUSTRY INITATIVE (NP-922) is not applicable. "

5. All well and water samples taken as required by Appendix 5B will be analyzed for tritum and Principal Gamma Emitters (PGE). PGE's are those as described-in Table 2.2-1, Note (3). All well and water sample taken as .required :by..:.:.,ý-

Appendix 5B will, at a minimum, be analyzed to meet the Lower Limit of Detection (LLD) on the Water Column of Table 5.1-3. In addition the LLD for tritum will be as low as practical that can be achieved for the equipment and sampling methods being used.

6. All well and water samples taken as required by Appendix 5B with a confirmed level of tritum activity, or PGE greater than the Lower Limit of Detection (LLD) on the Water Column of Table 5.1-3, determined during the current years sampling will be analyzed at least once per year for Sr-89, Sr-90, Fe-55 and Ni-63.

5B-1 6/4/07

7. The following wells will be sampled quarterly. Other wells and water samples may be added based on engineering analysis, hydrological assessments or sample results and trends.

Well Location G-21 Tallahassee Road extension, west of FPL property.

Sample from top and bottom.

G-28 Tallahassee Road extension, west of FPL property.

Sample from top and bottom.

L-3 West of Interceptor Canal, on Land-U property.

Sample from top and bottom.

L-5 West of Interceptor Canal, on Land-U property.

Sample from top and bottom.

STP-1 Northeast of PTN Sewage Plant-. - - -

P-94-2 North of Solids Settling Basin, east of PTN intake.

P-94-4 East of Dress-out Building, in the RCA.

PTPED-9 Northeast Corner of Neutralization Basin.

CD-1 Northeast Comer of Neutralization Basin.

5B-2 6/4/07

L-2008-130, Supplement to 2007 Annual Radioactive Effluent Release Report

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1.8 REFERENCES

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L-2008-130, Supplement to 2007 Annual Radioactive Effluent Release Report

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1.8 REFERENCES

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