U-602028, Semiannual Radioactive Effluent Release Rept,Jan-June 1992 Clinton Power Station
| ML20114A954 | |
| Person / Time | |
|---|---|
| Site: | Clinton  |
| Issue date: | 06/30/1992 |
| From: | Spangenberg F ILLINOIS POWER CO. |
| To: | NRC OFFICE OF INFORMATION RESOURCES MANAGEMENT (IRM) |
| References | |
| U-602028, NUDOCS 9208240161 | |
| Download: ML20114A954 (322) | |
Text
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l Ithnois Power ( ompany it Chn'on Power Stat;on E: P.O Box 678 Clinton. ;L 61727
' Tel 217 935-8881 ILLIN9tS u.602028 P& M R-U45-92 (08-18)LP 20.220 Atgust 18, 1992 i'F Docket No. 50-461 I- Document Control Desk
. Nuclear Regulatory Commission Washington,.D.C. 20555 Subj ec t: Clinton Power' Station Semiannual Radioactive Effluent release Report r
Dear Sir:
_Attachdd is the Semiannual Radioactive Effluent Release Report for Clinton Power Statior.- (CPS) for the period of January 1,1992 through .
-June 30, 1992. This submittal is provided in accordance with the requirements'of section'6.9.1.7 of the CPS Technical Specifications.
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Sincerely yours,
/*
F. A. Spangenberg, III Manager, Licensing and Safety SFB/msh' 3 .-
Attachment
- NRC Clinton Licensing P iject Manager NRC Resident Office cA NRC Region III, Regional Administrator Illinois Department of Nuclear Safety 92082401 PDR ADO hhh61P DR -
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Semiannual Racioactive Effluent Release Report 5'
January 1,1992 - June 30,1992 Clinton Power Station
January 1, 1992 - June 30, 1992 SEMIANNUAL RADIOACTIVE EFFLUENT RELEASE REPORT FOR THE CLINTON POWER STATION Prepared by
-Radiological Environmental Group Radiation Protection Department July 29, 1991
TABLE OF CONTENTS SECTION PAGE
- 1. . Executive Summary . . . . . . . . . . . . . . . . 5
- 2. Introduction. . . . . . . . . . - . . . . . . . . . 6 3 '. Supplemental Information. . . . . . . . . . . . . 15
- 4. Effluent and Waste Disposal Data. . . . . . . . . 22
- 5. Meteorological Data and Dispersion Estimates. . . 36
' 6. Dose Measurements and Assessments . . . . . . . . 48
- 7. Changes to the'Offsite Dose Calculation Manual. . 59
- 8. ODCM Operational Requirement Reports. . . . . . . 60
- 9. Major Changes to Radioactive Waste Treatment Systems - . . . . . . . . . . . . . . . . . . . .
. 61 10 .- -
New Locations for Dose Calculation and/or '
Environmental Monitoring. . . . . . . . . . . . . 62 4
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LIST OF-TABLES PAGE Table 1: . Airborne Effluents - Summation of All Releases . . . . . . . . . . . . . . . . . . 22
' Table 2: Airborne' Effluents . . . . . . . . . . . . . 23 Table 3: Radioactive Gaseous Waste LLD Values . . . . 25 Table 4: Waterborne Effluents - Summation of All Releases . . . . . . . . . . . . . . . . . . 27 Tabl'e 5: Waterborne Effluents . . . . . . . . . . . . 28 Tabla 6: Radioactive Liquid Waste LLD Values. . . . . 29 Table 7: Solid Waste'and Irradiated Fuel' Shipments. . 32 Table 8: Corrections to Data Reported in Previous Semiannual Reports . . . . . . . . . . . . . 34 Table 9: Effluent Data Not Available for Previous
-Semiannual Report. . . . . . . . . . . . . . 35 Table'10: Meteorological Data Availability . .. . . . 37 Table 11: Classification of Atmospheric Stability. . . 40 iTable 12: Joint Wind Frequency Distribution by Stability Class. . . . . . . . . . . . . . . 41 Table 13: Maximum Offsite Doses and Dose Commitments to Members of the Public . . . . 48 Table 14:-Calculated Doses to Members of the Public During Use of the Road in the Southeast.
Sector within the CPS Site Boundary. . . . . 52 Table :15 : Calculated-Doses to Members of the Public During Use of-the Agricultural Acreage in
- the. South-Southwest Sector within the CPS Site Boundary. . . . . . .. . . . .. .. . . . 53 Table 16: LCalculated Doses to' Members of the Public During Use of Clinton Lake in the Northwest Sector within the CPS Site Boundary. . . . . 54 2
.. . ~ . - .. . . - . . . - . - .- . . . . . - ..
LIST OF TABLES (con't)
PAGE Table 17: Calculated Doses to Members of the Public During Use of the Department of (
Conservation Recreation Area in the East-Southeast Sector within the CPS Site Boundary . . . . . . . . . . . . . . . . . . 55 Table 18: Calculated Doses for the Residents in the Southwest-Sector within the CPS Site Boundary . . . . . . . . . . . . . . . . . . 56 Table 19: Calculated Doses for the Residents in the West-Southwest Sector within the CPS Site Boundary . . . . . . . . . . . . . . . . . 57 Table 20: Calculated Doses for the Residents in the South-Southeast Sector within the CPS Site Boundary . . . . . . . . . . . . . . . . . . 58 3
LIST OF FIGURER PAGE Figure 1:-CPS Airborne Effluent Release Points-. . . . 7 Figure 2: CPS Waterborne Effluents Release Pathway . . 8 Figure 3: -Effluent Exposure Pathways . . . . . . . . . 13 Figure 4: CPS 1992 Monthly Liquid Rae'Laste Discharge Total. . . . . . . . . . . . . . . 21 Figure-5: CPS Wind Rose: 10-meter . . . . . . . . . . 38 Figure 6: CPS Wind Rose: 60-meter . . . . . . . . 39 Figure 7: Areas Within'the CPS Site Boundary Open to Members of the Public . . . . . . . . . . 51 1
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SUMMARY
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EXECUTIVE SUMM?.RY The Semiannual Radioactive Effluent. Release Report is a detailed description of all radioactive releases (both gaseous and liquid) from the Clinton Pover' Station (CPS) and the resulting radiation doses for tlui period from January 1, 1992 through June 30, 1992.
This report includes a detailed meteorological section which providesithe weather. history of the area during this period.
This information is used to calculate the dose to the public.
The report also. includes a summary'of the amounts of radioactive material contained in solid waste that is packaged and shipped for offsite disposal at federally-approved burial facilities. In addition, this. report notifies tne U.S. Nuclear Regulatory Commission ~(NRC) staff of changes to CPS's Offsite Dose Calculation Manual (ODCM) and exceptions to the CPS effluent monitoring program which must be reported per ODCM Operation Requirements 2.7.1.b and 3.9.2.b.
The NRC requires that nuclear power stations be designed, constructed, .and operated in such a way that the amount of radioactive material in affluent releases to unrestricted areas is kept As-Low As Beasonably Achievable ( ALARA) . To assure these criteria are met, the NRC has established limits governing the
-release offradioactivity in effluents.
CPS was operated in compliance with-established limits during
.this report period.. The maximum radiation dose delivered to the inhabitants of the area' surrounding CPS, due to radioactivity released from the station, was very small. The radiation dose to people in the vicinity of CPS was calculated for a continuous
. gaseous release by using the concentration of radioactive material and the weather conditions at the time of the release.
Radiation dose to the public was also calculated for liquid. batch releases using the concentration of radioactive material and the non-radioactive dilution flow at the time of the release. These doses were only a small fraction of the limit for the most exposed member of-the public.
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SECTION 2 INTRODUCTION e
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l INTRODUCTI_OH Clinton Power Station is located in Harp Township, DeWitt County
-approximately six_ miles east of the city of Clinton in east-c'ntral Illinois. Clinton Power Station is a 985 megawatt gross electrical power output' boiling water. reactor. The reactor =and generating units were supplied by General Electric, Sargent and Lundy Engineers served as architect-engineer, and BaldWin Associates was the constructor.
Construction of CPS began in the mid 1970's. Fuel load began in September of 1986 with initial criticality achieved on February 27, 1987. Commercial operation commenced in April 1987 and the reactor reached 100% power for the first time on September 15, 1987.
Airborne effluents are normally released from CPS via two gaseous effluent release points to the environment: the Common Station Heating, Ventilating, and Air Conditioning (HVAC) Stack and the Standby Gas Treatment System (SGTS) Vent (see Figure 1). Each' release point is continuously monitored and a program of periodic sampling and analysis is conducted as specified in the ODCM.
During this report period a third release point was briefly established. - .This release point was a decontamination system brought on site and located external to plant ventilation. The same sampling and analysis routines were established for-this as with the HVAC and SGTS systems. Liquid effluents from CPS are released in batch mode and are sampled ad analyzed prior to release. Liquid effluents, variable from 10-60 gallons per minute (gpm) or 50-300-gpm, combine with Plant Service Water flow (minimum of approximately 5000 gpm) and Plant Circulating Water flow (0-567,000 gpm) in the sealwell prior to entering the 3.4 mile discharge flume to Lake Clinton (see Figure 2).
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CPS AIRBORNE EFFLUENT RELEASE POINTS Figure 1 TURENE BVGING f%DWASTE AND ROOF EL 876'0' MAOHINE SHOP BUILDING /
ROOF EL 781'0'
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. 170'0' j 206'0' 3
HVAC VDfT STACK SGTS VENT TOP CONTAJNMENT CONO. EL 927'0* ,
9, CONTROL EU1LDWG
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FUEL BUILDING
__ . ROOF EL 800'0' ,
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f D!ESEL GEN. AND HVAC BUILDING
/ SGTS FILTER UNITS (n EL 71G'0')
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GASEQUS EFFLUENT RELEASE POINT CHARACTERISTICS HVAC EXHAUST ', TACK SGTS EXHAUST STACK RELEASE POINT HEIGHT (m) 61 61 BUILDING HEIGHT (m) 58 58 RELEASE FOINT GEOMETRY DUCT P1PE RELEASE POINT AREA (m') 11.15 0.15 RELEASE FOINT DIAMETER (m) 0.77' O.44 ANNUAL AVERAGE FLOW RATE (fr 8 / min) 237,000 4000 VERTICAL EXIT VELOCITY (m/ soc) 10.02 12.49 7
CPS WATERBORNE EFFLUENTS RELEASE PATHWAY !
Figure 2 PLANT SERVICE WATER
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RW BLDG- (AT LEAST 5000 GPM)
(UP TO 25.0C0 RE l, '
GALLONS /DATCH)
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LIOUID RADWASTE DISCHARGE LINE (10-60 OR 50-3CO GPM) h RADIATION MONITOR AL/JWTmP SETPOINT CALCULATED DASED ON EACH DATCH1SOTOPIC ANALYSIS AND DtLtmON FLOW r . >4 ISOLATION VALVE TERMINATES RELEASE ON HIGH RADIATION.
HtGH RELEASE FLOW RATE. OR Low @ COMPOSITE SAMPLER (
DIM ON W m COLLECTS APPROX %%TELY 20 ml EVERY 60 M'NUTES FROM Tite DISCHARGE FLUME FOR MONT11LY ANALYSIS SEALWELL 0 LAKE 3LANT CIRCULATING CLINTON WATER (0-567,000 GPia) DISCHARGE FLUME 3.4 MILES 8
Reculatory Limits The NRC requires nuclear power plants to be designed, constructed and operated-in such.a way.that the radioactivity in effluent releases to unrestricted areas-is kept ALARA. To assure these criteria are met, each license authorizing nuclear reactor operation includes Radiological Effluent Technical Specifications-
. (RETS) governing the release of radioactive effluents (Code of Federal Regulations, Title 10, Part 50, Appendix I). The RETS designate the limits for release of effluents, as well as the
- limits for doses to the general public from the release of radioactive-liquids and-gases. Keeping releases within these operating limits demonstrates that the ALARA principle is being met.
The dose to a member of the general public from radioactive material in liquid effluents released to unrestricted areas is limited to:
_Less than or equal to 3 mrem per year to the total _
-body.
-and-Less than or equal to 10 mrom per year to any organ.
The dose to air due to release of noble gases in gaseous
~ effluents is limited to:
Less than or equal to 10 mrad per year for gamma radiation.
-and-Less than or equal to 20 mrad per year for beta radiation.
The dose to a member of the general public from iodine-131, tritium and all particulate radionuclides _with a half-life greater _than eight days in_ gaseous effluents is limited to:
Less-than or equal to 15 mrem per year to any organ.
These ALARA limits are a fraction of the dose limits established c by.the Environmental Protection Agency (EPA). In its Environmental-Dose Standard of 40CFR190,-the EPA established dose it limits for members of the public in.the vicinity of a nuclear power: plant.- These-dose limits are:
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Less-than or equal to 25 mrem per year to the total
-body.
- Less than or equal to 75.mrom per year to the thyroid.
-and-Less than or equal to 25 mrem per year to any other organ.
See Section 3 for more information on regulatory limits.
Processina and Monitorinc Effluents are strictly controlled at' CPS to ensure radioactivity released to the environment is minimal and does not exceed release limits. Effluent controls include the operation of tidiation_ monitoring systems in the plant-and offsite environmental sampling and analysis programs. In-plant radiation monitoring systems are used to provide a continuous indication of radioactivity'and are also used to collect particulate and radiciodine samples. These samples are anelyzed in a laboratory to identify-the specific concentration of radionuclides being released. Sampling and analysis 1 provide a more sensitive and precise method of determining effluent composition to complement the information provided by real-time monitoring instruments.
Beyond the plant itself, a radiological environmental monitoring program is maintained in accordance with Federal Regulations.
The basic purpose of-the program.is to assess the radiological.
impact onLthe environment due.to the operation of the clinton Power Station. Implicit in this purpose is the regulatory requirement to trend and assess-radiation exposure-rates and radioactivity concentrations that may contribute to human radiation exposure. The program consists of two phases, preoperational and operational. During the preoperational phase ofLthe program, the baseline.for the local radiation environment was established. The operational phase of the program includes the objective of' making confirmatory measurements to verify-that the in-plant controls for the' release of radioactive material are functioning as designed. Assessment of'the operational impact of CPS on the environment is based op data collected since initial reactor criticality.
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Exnosure Pathways Radiological exposure pathways are the means by which people may become exposed to radioactivity released from nuclear facilities.
The major pathways of concern are those which These could are pathways cause the determined highest calculated radiation dose.
from the type and amount of radioactivity released, the environmental transport mechanism and use of the environment.
The environmental transport mechanism includes the meteorological characteristics of the area which will be defined This by wind speed information and wind direction at the time of the release.
is used to evaluate how the radionuclides will be distributed in the area. The most important factor in evaluating the exposure pathway is the use of the environment by the people living around CPS. Factors such as location of homes in the area, use of cattle for milk and meat, and the growing of gardens for vegetable consumption are veryFigure important considerations 3 illustrates in the various evaluating exposure pathways.
effluent exposure pathways considered.
The radioactive gaseous effluent exposure pathways include direct radiation, deposition on plants and soil, and inhalation by animals and humans. The radioactive liquid effluent exposure pathways include drinking water, fish consumption and direct exposure from the lake.
Dose Assessment in the Whole body radiation involves the exposure Most of all organs background radiation human body to ionizing radiation.
exposures consist of whole body expocure although specific organs can receive radiation exposure from distinct radionuclides.
These radionuclides enter the body through inhalation nuclide. and ingestion and seek different organs depending on tha '
For example, radioactive iodine selectively concentrates in the thyroid, radioactive cesium collects in muscle and liver tissue, and radioactive strontium in mineralized bone.
The total dose to organs from a given radionuclide also depends on the amount of activity in the organ and the amount of time that the radionuclide remains in the body. Some radionuclides remain for very short periods of time due to their rapid radioactive decay and/or elimination rate from the body, while others may remain longer.
The radiation dose to people in the area surrounding CPS is calculated for each release using the concentrations of radioactive material and the weather conditions present at the time of the release. The dose is calculated ininto all account sixteen the geographical sectors surrounding CPS and takes location of the nearest residents, vegetable gardens producing f
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broad leaf!. vegetables,-dairy and meat animals in all sectors.-
The calculated dose alco uses the concept of a " maximum-exposed individual" and " standard man", and the maximum use factors for the environment, such as how much milk an average person drinks and how much' air that-person breathes'in a year.
See Tables' 13- 20 of Section 6 for more detailed information' on dose-_to.the public.
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f RELEASES DILUTED BY ATMOSPHERE
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Gaseous Effluents--
Gaseous effluent radioactivity released from CPS is classified !
.into two categories, 1) noble gas, and 2) iodine-131, iodine-133,
' tritium and all radionuclides-in particulate form with half-lives greater than.eight' days. Noble gases, such as xenon and krypton, are biologically and chemically nonreactive; these radionuclides cause external radiation exposure. Iodine-131, iodine-133,
-tritium and radionuclides in particulate form with half-lives greater than eight days are the major contributors to internal dose.
Noble gas was released during the first half of 1992 because of off ga3 system operation in the bypass mode for a five day period while at power and because of the performance of process radiation monitor calibrations.
See Tables 1, 2, 3 and 9 of Section 4 for more detailed information on gaseous effluents.
Liauid Effluents Radioactivity in liquid effluents consists of radioactive fission and activation prodi' cts, tritium and entrained noble gases.
See' Tables 4, 5, 6 and 9 of Section 4 for more detailed information on liquid effluents.
Solid Waste Shioments In order to reduce the radiation exposure to personnel and maintain the.ALARA concept, the NRC and the Department of Transportation (DOT) have established limits on the. types of radioactive waste and the amount of radioactivity that may be packaged and shipped offsite for burial or disposal. To ensure that CPScis complying with-these regulations, the types of waste and the radioactivity present are-reported to the NRC.
y See Table 7 of Section 4 for more--detailed information on solid waste shipment: .
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m -e4b.D>- d6 SECTION 3 SUPPLEMENTAL INFORMATION d
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I. -REGULATORY ~ LIMITS
.- A . _ Gaseous Effluents
- 1. In accordance with Title 10 of the Code of Federal Regulations (CFR), Part 20, the maximum permissible concentrations for gaseous effluents shall not-exceed the values given in 10CFR20, Appendix B,. Table II, Column 1. To ensure these concentrations are not exceeded, dose rates due to radioactive-materials released in gaseous effluents from the site to areas at and beyond the site boundary shall be limited to the following:
- a. Noble gases - Less than or equal to 500 mrem / year to the total body.
Less than or equal to 3000 mrem / year to the skin.
- b. Iodine-131, iodine-133, tritium and all radionuclides in particulate form with half-lives greater than eight days:
Less than or equal to 1500 mrem / year to any organ.
- 2. In accordance with Ti".e 10 of the Code of Federal Regulations, Part 50, Appendix I, air dose due to r noble gases _ released in gaseous effluents to areas at and beyond the site boundary shall be limited to the followina:
L a. LessLthan or equal to 5 mrad for gamma l radiation _-and less-than or equal to 10 mrad for-beta radiation-during'any calendar quarter.
l b. Less than or equal to 10 mrad for gamma L radiation and less than or equal to 20 mrad l for beta radiation during any calendar year, i l
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- 3. In accordance with 10CFR50, Appendix I, dose to_a ,
member of the public (from iodine-131, iodine-133,
, tritium and all-radionuclides in-particulate form l L with half-lives greater-than eight days) in I 15
. _ . . . . _. . . _ _- . _ _ _ _ _ _ _ . - _ . _ . . .._.m-_.-__--_m.
J gaseous effluents-released to areas at.and beyond the site boundary shall be limited to the-following:.
- a. Less than or equal to 7.5 mrem to any organ,
'during any. calendar quarter.
- b. Less than or equal to 15 mrem to any crgan, during any calendar year. ;
1
. Liquid Effluents B.
- 1. The concentration of radioactive material released in liquid effluents to unrestricted areas shall be -l limited toithe concentrations specified in Title !
I 10-of the Code of Federal Regulations, Part 20, Appendix B, Table II, Column 2, for radionuclides- !
other than dissolved or entrained noble gases. For dissolved or-entrained noble gases, the concentration shall be limited to 2.00E-04 microcuries per milliliter total activity.
- 2. The dose or dose commitment to a member of the public.from radioactive materials in liquid effluents released to unrestricted areas shall be limited'to:
- a. Less than or equal to 1.5 mrem to the total body and less tian or equal to 5 mrem to any organ during_any calendar quarter.
b.- Less than or equal to 3 mrem to the total body and less than or equal to 10 mrem to any organ during: any calendar year.
II. . MAXIMUM-PERMISSIBLE: CONCENTRATION A. Gaseous- -
- 1. - The maximum permissible concentrations (MPC) for -
gaseous effluents areispecified in Title 10 of the
. Code _of Federal Regulations, Part/20,_ Appendix B, TableHII, Column 1. However,_the MPCs of 10CFR20 are not utilized directly for limiting-gaseous effluents. -The CPS ODCM establishes requirements-to limit the release rate of effluents such that discharges of gaseous-radioactive material will>
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Enot result in dose rates, to a MEMBER OF THE PUBLIC in an UNRESTRICTED AREA , higher than thoso-which would occur if average annual concentrations exceeded-MPC limits. -The maximum permissiblo dose rates for gaseous. releases are:
- a. ODCM Operation Requjrement 3.4.1.a (Dose rate
-at and beyond the site boundary from gaseous effluents in tne form of noble gases).
Less than or equal to 500 mrom/ year to the total body.
Less than or equal to 3000 mrem / year to the skin.
- b. ODCM-Operation Requirement 3.4.1.b (Dose rate at and beyond the site boundary from gaseous effluents in the form of iodine-131, iodine-133, tritium and all radionuclides in particulate form with half-lives greater than eight days).
Less than or equal to 1500 mrem / year to-any organ.
B. Liquids
- 1. The maximum permissible concentrations (MPC) for
~
liquids-arc those listed in 10CFR20, Appendix B, Table II, Column 2, with the most restrictive MPC (whether soluble or insoluble) being used in all ceses. For dissolved and entrained noble gases the MPC of 2.00E-04 microcuries per milliliter is applied. This MPC is based on the Xe-135 MPC'in air (submersion. dose).' converted to an equivalent concentration in water as discussed in-the International Commission on Padiological Protection ' (ICRP) , Publication 2.
~
--III. AVERAGE ENERGY The CPS ODCM linits the dose equivalent rates due to the release of-fission and activation gases to less than or equal-to 500 mremfper year to the total' body and less-than or equal.to 3000 mrem per year to the skin.- Therefore, the average beta.and gamma energies (E) for gaseous effluents n
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as: described 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", is not applicable.
IV. MEASUREMENT AND APPROXIMATIONS OF TOTAL RADIOACTIVITY A. Fission and Activation Gases
- 1. Gas samples are collected at least weekly and are counted on a high purity germanium (HPGe) detector for principal gamma emitters. The HVAC and SGTS release points are continuously monitored, and the average release flow rates for each release point are used to calculate the total activity released in a given time period.
- 2. Trl' a is collected at the same frequency as the gau aumples by passing a known-volume of the sample stream through a gas washer containing a known quantity of_ demineralized water. The collected samples are distilled and analyzed by liquid-scintillation. The tritium released was calculated for each release point from the measured tritium concentration, the volume of-the sample, the tritium collection efficiency, and the atack' exhaust. flow rates.
B. lodines
-Iodine is continuously collected on a charcoal cartriMge-filter _via an isokinetic sampling assembly on each release point. Filters ~are normally exchanged once per week _and analyzed on an HPGe system. The daily average flow rates for each release point are averaged for the duration of the sampling period and L these results,_along with isotopic concentrations, are tuned to determine total activity released during the time period in question. ,
C.- .Particulates Particulates-are continuously collected on a filter paper via an ' isokinetic sampling assembly (n1 each
~
release point. Filters are normally exchanged once-per week: and analyzed on .an -HPGe system. Flow rates and total activity are determined in the same manner as for iodines.
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D. Liquid-Effluents Each tank of liquid radwaste is-sampled and analyzed for principal' gamma emitters prior to release._ Each 4 sample tank is recirculated for a sufficient amount of time prior to sampling to ensure that a representative sample is obtained. Samples are analyzed on an HPGe system and release permits are generated based on the values obtained from the isotopic analysis and from the most recent values forlthe analysis of tritium,. gross alpha, iron-55, strontium-89 and strontium-90. An aliquot based on release volume is saved and added to composite containers. The concentrations of composited isotopes and the volumes of the releases associated-with these composites establish the proportional relationships that are then utilized for calculating the total activity released for these isotopes.
'V.- BATCH RELEASES i
A. Liquid 1st Otr 92 2nd Otr 92
- 1. -Number of batch releases: 11 5
- 2. Total time period for batch releases: 967 min. 416 min.
- 3. Maximum time period for batch release: 95 min. 90 min.
- 4. Average time i period for batch release: 88 min. 83 min.
- 5. Minimum time period for batch release: 85 min. 70 min.
- 6. Average stream flow during periods of release: 1.86E+04 5.63E+04 liters per minute
- 7. Total waste volume: 1.01E+06 4.39E+05 liters
- 8. Total = dilution volume: 1.79E+07 2.37E+07 liters 19 i
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l B. Gaseous
~
1st Otr 92 2nd Otr 92 t
- 1. Number of batch releases: 0 0
- 2. -Total time period for batch releases: N/A N/A
- 3. Maximum time period for
. batch release: N/A N/A
- 4. Average time period *or
-batch release: N/A N/A
- 5. Minimum time period for batch release: N/A N/A VI. DESCRIPTION OF~ ERROR ESTIMATES A. Gaseous and Liquid Effluents Estimates of measurement and analytical error for gaseous and liquid effluents are calculated as follows:
ET= [(E1 )2 + (E2) + ...(En) 3 where, ET = total percent error El....En = percant error due to calibration standards, laboratory analysis, instruments, sample flow, etc.
20
-- ., ..-,-,2-.-._,
F GURE ^
CLlh- O N 30W E 1 STA~~lO 4
'1992' MONTHLY LIQUID RADWASTE DISCHARGE TOTAL'-
500 1
i
.400 -
F m
~
g 300 -
$3 ;
S8
_j J '
h$ 195.390 'W 6 200 -
n /
100 - '
48.504 44,214 47,969 i 7: 23,760 .-*
0 .. LYb hh ',k JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DECTOTAL
4, 6- - * *+ % 4 s Ase ,A.A A4~# aL= 1 -is, an#+ _ 6 -a, l
SECTION 4 .
EFFLUEXT AND- WASTE DISPOSAL DATA T
r e--w- e .-,- ,s- < > -- - r -,--,e --- e
l TAD _LR 1 AIRDORNE EFFLUENTS - SUMMATION OF ALL RELEASES Data Period: Januory 1, 1992 - June 30, 1992 Est Continuous Modo Total l Nuclido Category Unit 1st Quartor 2nd Quarter Error, %
'A . Fission & Activation Gasos
- 1. Total Release 2 Ci 0.00E+00 6.04E+00 30
- 2. Average Roloase Rate for Porlod pC1/ soc 0.00E+00 7.68E-01
- 3. Percent of Applicablo Limit % 0.00E+00 1.48E-03 B. Iodino-131
- 1. Total Rolosso Ci 2.50E-05 1.54E-05 31
- 2. Average Releaso Rato for Period yCi/sec 3.18E-06 1.96E-06 '
- 3. Porcent of Applicablo Limit % 3.76E-03 2.32E-03 C. Particulates
- 1. Particulatou Released with Half-lives >8 Days Ci 8.23E-04 1.16E-04* 24
- 2. Average Release Rato for Period pCi/sec 1 05E-04 1.48E-05*
- 3. Porcent of Applicable Limit % 9.55E-05 1.56E-07*
- 4. Gross Alpha Activity Released C1 3.67E-07 1.34E-06 D. Tritium
- 1. Total Release Ci 1.46E+00 4.96E-01 105
- 2. Avorage Release Rato for Period 4C3 see 1.86E-01 6.31E-02
- 3. Percent of Applicable Limit % 7.81E-05 2.65E-05 1 It should be noted that the lower the actual samplo activity is with respect to background t,,tivity, the greater the counting error- Largo errors are reported for the various components of 'PS gaseous offluents because of consistently low samplo act_vity.
? Notation: An erf ry of _0.00E+00 does not represent the absence of a radionuclido but indicates that the concentration of tho'nuclide was below-the Lower Limit of Detection (LLD) valuo' listed in Table 3.
- Reported values include Sr-89 and Sr-90 values based on first quarter 1992 samples analyson and second quarter 1992 ventilation exhaust ratos.
22
TADLE 2 AIRDORNE EFFLUENTS (Curies)3 Data Period January 1, 1992 - June 30, 1992 Continuous Mode Nuclide First Quarter Second Quarter A. Gases Kr-85 0.00E+00 1.91E-04 Kr-85m 0.00E+00 2.29E-01 Kr-87 0.00E+00 1.04E+00 Kr-88 0.00E+00 0.00E+00 Xe-127** 0.00E+00 3.54E-01 Xe-131m 0.00E+00 3.73E-05 Xe-133 0.00E+00 1.62E-03 Xe-133m 0.00E+00 1.08E-07 Xo-135 0.00E+00 0.00E-00 Xo-135m 0.00E+00 6.82E-01 Xe-137 0.00E+00 2.2?E-01 Xe-138 0.0"E+00 2.95E+00 Others: ,
Ar-41 0.00E+00 5.60E-01 Total 0.00E+00 6.04E+00 E. Iodines I-131 2.50E-05 1.54E-05 I-132 0.00E+00 0.00E+00 I-133 8.80E-06 0.79E-05 I-134 0.00E+00 0.00E+00 A 0.00E+00 0.00E+00 Total 3.38E-05 2.42E-05 C. Particulates w/ Half-lives
.>8 Days Sr-89 0.00E+00 0.00E+00*
Sr-90 0.00E+00 0.00E+00*
Cs-134 0.00E+00 0.00E+00 Cs-137 0.00E+00 0.00E+00 Da-140 0.00E+00 0.00E+00
_~
3 Notationt'An entry of 0.00E+00 does not represent the absence of a radionuclide but indicates that the concentration of the nuclide was below the LLD value listed in Table 3.
- Reported values are estimated based on first quarter 1992 composite analyses and second quarter 1992 ventilation exhaust rates.
- Xe 127 was used for monitor calibration. However, for dose considerations, this value was calculated as Xe 135.
23
-, . . . -. .. - .- - _ - _ - . -. . - . ... . - - _ . . . - - ~ . - . _ _ - . . . . .
_TADir 2 (conted), i AIRDORNE EFFLUENTS (Curics)3 Data Period: January 1, 1992 - June 30, 1992 Continuous Motic '
Nuclide 1st Quarter 2nd Quarter Others:
Cr-51 7.88E-04 1.16E-04 Mn-54 7.84E-06 0.00E+00 Co-58 0.00E+00 0.00E+00 Fo-59 0.00E+00 0.00E+00 Co-60 2.74E-05 0.00E+00 -
Zn-65 0.00E+00 0.00E+00
.Ag-110m -0.00E+00 0.00E+00 Co-141 0.00E+00 0.00E+00 co-144 0.00E+00 0.00E+00 Total 8.23E-04 1.16E-04 3 -Notation: An entry of 0.00E+00 does not represent the absenre of a radionuclide but indicates that the concentration of the nuclide was below the LLD value listed in Table 3.
24
l l
TABLE 3 RADIOACTIVE GASEOUS WASTE LLD VALUES LOWER LIMIT OF TYPE OF DETECTION (LLD)a ACTIVITY ANALYSIS fuci/ml)
Principal Gamma Emitterab,c 1xto-4 H-3c 1x10-6 I-131 d 1x10-12 I-133 d 1x10-10 Principal Gamma Emittersb ,o 1x10-11 (I-131, others)
Gross Alpha f 1x10~11 Sr-89, Sr-909 1x10-11 Table 3 Notations aThe LLD is defined, for purposes of these specifications, as-the smallest concentration of radioactive material in a sample that will yield a not 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:
4.66 sb LLD =
E x V-x 2,22 x 10 6 x Y x exp (-AAt) 25
_ _ _ , . .,. ,. _ _ . . - _ . _ _ . . - . _ - , . . ~ , . . _ . _.___. _ .-~.._._ _._ . . . _ _ . _ _ _ _ _ . . . _
- - - . . . - _ - . . - - - - - .- -. -. _ ~ - . . - . - . - - - _ . - - -
Table 3 fintations (Cont'd)
Where:
i LLD in the "a priori" lower limit of detection as defined above, as microcuries per unit mass or volume, sb is the standard deviation of the background counting rate or of the ccunting rate of a blank sample as appropriate, as counts'per minute, E'is the counting efficiency, as counts per disintegration, V is the sample size in units of mass or volume, 2.22 x 10 6 is the number of disintegrations per minute per microcurie, I
Y is the fractional radiochemical yield, when applicable, A is the' radioactive decay constant for_the particular radionuclide (sec~l)-and at for plant effluents is the elapsed time between the midpoint of sample collection and the time of counting (sec). ,
Typical values of E, V, Y, and at should be used in the calculation.
It should be recognized that the LLD is defined as an a oriori (before the-fact) limit representing the capability of a
-measurement system and not as an a costeriori (after the fact) limit for a particular measurement.
b The principal gamma _ emitters for which the-LLD specification applies include the following radionuclides: Kr-87,-Kr-88, Xe-133, Xe-133m, Xe-135, and Xe-138 in noble gas releases and Mn-54, Fe-59, Co-58, Co-60, Zn-65, Mo-99, I-131, Cs-134, Cs-137,-
Ce-141 and Co-144 inLiodine and particulate releases. This list does not mean that only these nuclides are to be considered.
Other gamma peaks that are identifiable, together-with those of the above nuclides, shall also be analyzed.and reported in the Semiannual Radioactive Effluent Release Report, cManthly grab s,mple and analysis d Continuous charcoal sample analyzed weekly
" Continuous particulate-sample analyzed weekly f
Composite particulate sample analyzed monthly 9Composite particulate sample analyzed quarterly 26
5 i
TADLE 4 WATERDORNE EFFLUENTS - SUMMATION OF ALL RELEASES Data Periodt January 1, 1992 - June 30, 1992 BATCH MODE Est. Total Nuclide Category Unit 1st Quarter 2nd Quarter Error, %
A. Fission & Activation Products
- 1. Total-Release Ci 7.31E-03 2.73E-03* 17
- 2. Average Diluted '
Concentration pCi/ml 3.87E-07 1.13E-07*
- 3. Percent of Applicable Limit % 7.86E-02 1.44E-01*
B. Tritium- ;
- 1. Total Release C1 1.24E+00 7.53E-01 16
- 2. Average Diluted Concentration pCi/ml 6.56E-05 2.29E-05
- 3. Percent of Applicable Limit. % 2.37E-01 4.13E-01
-- C . Dissolved and Entrained Gasgs
- 1. Total Release Ci 0.00E+00 0.00E+00 11+
- 2. Average Diluted Concentration pCi/ml 0.00E+00 0.00E+00
- 3. Percent of Applicable Limit % 0.00E+00 0.00E+00 D. Gross Alpha Radioactivity Released Ci 0.00E+00 0.00E+00 57 E. Volume of Waste gal. 2.67E+05 1.16E+05 11 Released liters 1.01E+06 4.39E+05 F. Volume cf Dil'1 tion gal. 4.73E+06 6.26E+06 2.6 Water Used liters 1.79E+07 2.37E+07
- Reported values include Fe-55, Sr-89 and Sr-90 values based on first quarter 1992 sample analyses and second quarter 1992 discharge volumes.
4 Notation: An entry of 0.00E+00 does not represent the absence of a radionuclide but indicates that the concentration of=the nuclide was below the LLD value listed in Table 6.
+ This error is associated with the gamma spectroscopy system, even though noble gas activity is <LLD.
27
_ . - . _ _ . _ _ - ___ _ ~. ._. , _
TADLE_1 WATERBORNE EFFLUENTS (Curies)5 Data Period: January 1, 1992 - June 30, 1992 Batch Mode Nuclide 1st Quarter 2nd Quarter A. Tritium 1.24E+00 5.53E-01 B. Fission & Acti-vation Products Cr-51 1.66E-03 0.00E+00 Mn-54 1.13E-03 5.91E-04 Co-58 4,80E-04 3.49E-04 Co-60 3.43E-03 1.63E-03 Fe-55 3.64E-04 1.58E-04*
Fe-59 2.43E-04 0.00E+00 Zn-65' O.00E+00 0.00E+00 Sr-89 0.00E+00 0.00E+00*
Sr-90 0.00E+00 0.00E+00*
Mo-99 0.00E+00 0.00E+00 Sb-124 0.00E+00 0.00E400 I-131 0.00E+00 0.00E+00 I-133 0.00E+00 0.00E+00 I-135 0.00E+00 0.00E+00 Cs-134 0.00E+00 0.00E+00 Co-137 0.00E+00 0.00E+00 Ba-140 0.00E+00 0.00E+00 La-140 0.00E+00 0.00E+00 Co-141 0.00E+00 0.00E+00 Ag-110m 0.00E+00 0.00E+00 Total 7.31E-03 2.73E-03 C. Dissolved and Entrained Gases Kr-85 0.00E+00 0.00E+00 Kr-85m 0.00E+00 0.00E+00 Kr-87 0.00E+00 0.00E+00 Kr-88 0.00E+00 0.00E+00 Xe-133 0.00E+00 0.00E+00 Xe-133m 0.00E+00 0.00E+ra Xe-135 0.00E+00 0.00E+00 Xe-135m 0.00E+00 0.00E+00 Xe-138 0.00E+00 0.00E+00 Total 0.00E+00 0.00E+00 v
5 Notation: An entry of 0.00E+00 does not represent the
-absence of a radionuclide but indicates that the concentration of the nuclide was below the LLD value listed in Table 6.
- Reported value is estimated based on first quarter 1992-sample analyses and second quarter 1992 discharge volumes.
28
TADLE 6 RADIOACTIVE LIQUID WASTE LLD VALUES LOWER LIMIT OF TYPE OF DETECTION (LLD)a ACTIVITY ANALYSIS (uCi/ml)
Principal Gamma Emitters b 5x10~7 I-131 1x10-6 Dissolved and Entrained Gases 1x10-5 (Gamma Emitters)
H-3 1x10-5 Gross Alpha 1x10~7 Sr-89, Sr-90 5x10-8 Fe-55 1x10-6 I.able 6 Notations aThe LLD is defined, for purposes of these requirements, as the smallest concentration of radioactive material in a sample that will yield a net count, above system background, that will be detected with 95% probability with only 5% probability of falsely concluding that a blank observation represents a "real" signal.
For a particular measurement system, which may include radiochemical separation:
4.66 sb
~
E x V x 2.22 x 10 6 xyx[xp (- A At) 29
Table 6 Notations (Cont'd)
Where:
LLD is the "a priori" lower limit of detection as defined above, as microcuries per unit mass or volume, sb is the standard deviation of the background counting rate or of the counting rate of a blann sample as appropriate, as counts per minute, E is the counting efficiency, as counts per disintegration, 1
V is the sample size in units of mass or volume, 1 2.22 x 10 0 is the number of disintegrations per minute per microcurie, Y is the fractional radiochemical yield, when applicable, A
is the radioactly)e radionuclide decay constant for the particular (sec~ and at for plant ef fluents is the elapsed time between the midpoint of sample collection and the time of counting
-(sec).
Typical values of E, V, Y, and at should 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 nosteriori (after the fact) limit for a pLrticular measurement.
b The' principal gamma emitters for which the LLD rea".irement
. applies include the following radionuclides: Mn-54, Fe-59, Co-58, Co-60, 2n-65, Mo-99, Cs-134, Cs-137, and Co-141. ~
Co-144 shall also_be measured, but with an LLD of 5 x 10 . This list does not mean that'only these nuclides are to be detected and reported. Other gamma peaks that are measurable, together with-those.of the above nuclides, shall.also be analyzed and reported in the Semiannual Radioactive Effluent Release Report.
30
SOLID WASTE AND IRRAQlhTRD FUEL SHIPMENTS During this reporting period there were thirty-two (32) radioactive waste shipments and no irradiated fuel shipments from CPS as reported in Table 7. All waste shipped in this reporting perlud was classified as Class A. In addition, CPS Technical Specifications, section 6.9.1.7 requires reporting of the ,
following information for solid waste shipped offsite during the l report period:
ft3, 135.8 ft3 , 177.9 ft3, 178.9 ft, 3 1.
Containeg 183.2 ft , volumeft}3.5 1173 *.
- 2. Total curie quantity: 1002.32 curies as determined by dose-to-curie and sample concentration methodology estimates.
- 3. d principal ra'ionuclides: See Table 7, A.2 for listing of measured radionuclides.
- 4. Source of waste.and processing employed: Resins, filter sludges and evaporator bottoms dewatered or solidified in cement, and non-compacted dry active waste.
- 5. Type of container: LSA, Type A, and Strong Tight Container.
6 Solidification agent or absorbent: Cement.
- This container was shipped to a waste processor, not a disposal site, 31 e- -e.'g. yy m' -'
ymm'eWn'+
TADLE_2.
SOLID WASTE AND IRRADIATED FUEL SHIPMENTS January 1, 1992 - June 30, 1992 A. SOLID WASTE SHIPPED OFFSITE FOR BURIAL OR DISPOSAL (not irradiated fuel) 6-MONTH EST. TOTAL
- 1. TYPE OF WASTE UNIT PERIOD ERROR, %
- a. Resins, m3 1.37E+02 filter sludges, C1 1.00E+03 25.0 evaporator bottoms, etc.
- b. Dry compactible m3 1.34E+01*
waste, contaminated C1 2.32E+00 25.0 equipment, etc.
c.- Irradiated components m3 0.00E+00-control rods, etc. Ci 0.00E+00 0
- d. Other m3 0.00E+00 Ci 0.00E+00 0
- ACTUAL DISPOSAL VOLUME FROM WASTE PROCESSOR
- 2. ESTIMATE OF-MAJOR HUCLIDE COMPOSITION 2 NUCLIDE PERCENT NAME ABUNDANCE CURIES
- a. Fe-55 56.20% 5.62E+02 Co-60 29.20% 2.92E+02 Mn-54 6.63% 6.63E+01 H-3 2.96% 2.96E+01 Cr-51 2.63% 2.63E+01 OTHER 2.38% 2.38E+01
- b. Fe-55 64.30% 1.49E+00 Co 16.40% 3.80E-01 Cr-51 10.70% 2.40E-01 Mn-54 4.10% 9.51E-02 H-3 3.40% 7.89E-02 C-14 1.10% 2.55E c. NONE N/A N/A
- d. NONE N/A N/A 4
32
.. - - - ~ - . - _ - - _ . - . . _ _ .
- . . - . . ~ - . - . _ - . . . . - . . - . - - . ~ . . _
4 TADlE 7 (Cont'd)
SOLID WASTE AllD IRRADIATED FUEL Bl!IPMENTS January 1, 1992 - June 30, 1992
- 3. SOLID WASTE DISPOSITIOli NUMBER OF SiiIPMEllTS MODE OF TRAllSPORTATION DESTINATIOli 24 Truck Richland, WA 4 Truck Barnwell, SC 8 Truck Oak Ridge, T!!
B. IRRADIATED FUEL SilIPMENTS (Disposition)
NUMBER OF SilIPMENTS MODE OF TRANSPORTATION DESTINATION NONE N/A li/A 1
l l.
t-l L
1.
33
i l
TABLE 8 CORRECTIONS TO DATA REPORTED IN !
PREVIOUS SEMIANNUAL REPORTS i t
CORRECTIONS TO DATA REPORTED IN PREVIOUS SEMIANNUAL REPORTS. f I
I. Correction to the Maximum Offsite Doses and Dose Commitments to Members of the Public.
A. Parameter of concern Second half of 1991, Table 13, Section B, Item 1.
- 1. a) Reported 4th Quarter Total Body Valuct i 5.25E-05 b) Corrected 4th Quarter Total Body Values 4.71E-05 ;
+
1 4
}
34
+ ~. - - r . - -, :- - .: --. . - . . . - , . , - - . - . . - . . - - , . . . . . , . - , _ - . - . .-- . .~.
TADLE._1 EFFLUENTDATANOTAVAILABLE{0R PREVIOUS BEMIANNUAL REPORT Data Periods October 1, 1991 - December 31, 1991 Nuclide Category Unit Fourth Quarter 1991 A. Airborne Ef.fluents
- 1. Sr-89 Ci 4.54E-06
- 2. Sr-90 Ci 0.00E+00 B. Waterborne Effluents
- 1. Fe-55 Ci 0.00E+00
- 2. Sr-89 Ci 0.09E+00
- 3. Sr-90 Ci 0.00E+00 E
f 6- Notation: An entry of 0.00E+00 does not represent the absence of a radionuclide but indicates that the concentration was below the LLD value listed in Table 3.
35
,- .- . - , _ , . . ~ - _ , _ . . _ _ , . , _ _ . _ . _ .- . _ - . - _ -. __ _
1 l
l i
1 i
n SECTION 5 METEOROLOGICAL DATA
a - -- - - - - -- - +a -2__ J A-__ .m a E
SECTIOX 5 .
METEOROLOGICAL DATA
1 l
l l
EFTEOROLOGICAL DATA AND DISPERSION ESTIMATER The meteorological monitoring program began at the Clinton Power ,
Station site on April 13, 1972. The meteorological system consists of a tower 199 feet high with two levels of instrumentation, at the 10-meter and 60-motor levels. Wind directions and speeds at the 10-meter and 60-meter levels are measured by a combined cup and vane sensor. The temperature at these levels is sensed by an aspirated dual temperature sensor.
One-half of the dual sensor at each elevation is used for ambient temperature while the cther half is used to provide a differential temperature between the 10-meter and 60-meter levels. Dew-point is measured at the 10-meter level with an aspirated dow point sensor. Precipitation is measured at ground '
level by a tipping bucket rain gauge.
Meteorological monitoring instruments have been placed on the Clinton Power Station microwave tower at the 10-meter level to act as a backup to the existing meteorological tower.
Clinton Power Station meteorological data is transmitted to the Main Control Room via a dedicated telephone line. There the signals are receive? and converted to a 4 to 20 milliamp signal and. fed indit!. dually to a microprocessor and chart recorders.
The microprocessor is part of the Clinton Power Station Radiation
-Monitoring System. Meteorological data is available via the microprocessors in the Main Control Room, Technical Support Center and Radiation Protection office.
Dispersion modeling for effluents for normal operation of Clinton Power Station is a straight-line, sector-averaged Gaussian plume model designed to estimate average relative concentration at various receptor points. The model was developed in accordance with routine release analysis procedures specified in Regulatory Guide 1.111. For joint frequency input data, periods of calm are distributed in accordance with a directional distribution. For hourly input data, periods of calm are accigned the previous hour's wind direction. Periods of calm are assigned a wind speed value of half the specified instrument threshold value. See Tables 10-12'and Figures 5-7 for more detailed information on meteorology-and dispersion data.
A problem with the meteorological monitoring instrumentation was discovered in 1991.- This problem caused stability class determination to be in error and was corrected in January.of this year. Previously reported values affected by stability class are being evaluated for accuracy at this time.
36 4
TABLE 10
- METEOROLOGICAL DATA AVAILADILITY Data Period: January 1, 1992 - June 30, 1992 Percent of Valid Paramqtat Hours Durina Period ,
- 1. Wit.d Speed i i
- a. 10-meter Sensor 97%
- b. 60-meter Sensor 97%
- 2. Wind Direction
- a. 10-meter Sensor 97%
- b. 60-meter Sensor 97%
- 3. Temperature
- a. 10-meter 97%
- b. Temperature Difference (10m-60m) 97%
- 4. Percent of hours for which valid 96.6%
10-meter Wind Speed, Wind Direction,
& Delta Temperature were available 5.-Percent of hours for which valid 96.6% '
60-meter Wind Speed, Wind Direction,
& Delta Temperature were available k
+
37
. .. . - .. :---. .- -, -v-.;--,.._ _ _ . _ . . . . , , . , . ,-. . _ . - _ - - ,
I figure 5 i CPS Wind Rose: to - Meter Data Period: January 1,1992 - June 30,1992 i
N l
7.4%
S.7% h NNE 6.1%
o g& l NW NE 6.9% ijj 6.9%
. l-1
.r y
, s .;
a
',:0 a
y
- .g.g
+.
$9' 5.3%
'y ; ENE 5.7%
s.
2 .
) l ,k '
m l /\
xi<
'V !
59% .k' bbMMIIX E /
O 5 55
~'
'.' ,)
i.
- '\ ,
/'
6% ,
,- :j ^ l '
, s i.
EW SE 5.3% 6.7%
. s ,
,;7 WIND SPEED TEXT-Q( yri un h, >24 WPH Qj lt -24 MPH SSE p SSW 8.1%
6.4% d 13-18 MPH S
!- 8-12 MPit 8.1% '
( ') 4-7 MPH
' $ 1-3 uns
. ~ _ . . _ . _ _ . _ . .
Figure 6 s.l.
CPS Wind Rose: 60 - Meter a:
L.1 Data Period: January 1,1992 - June 30,1992 3
i*i s N
, 8.0%
, IJJW - gyg
.t- 6.7% 5.4 %
b D
IN '@ ,
6.7% 1m Gj NE S.7% >
My..
if$ _
'Q . jfy -
% ._ .]
- c. 'i My '
1 ,
WNW $ ENE 4.3% :? 5.8%
- ); , '
>, g M , f w,r m
=
s
/ \
\
i' 5.$% Y $$I( W ///) Y ,
0,2%
DV////$b 60%
A 4 ,
N
~
\ -
WSW- ESE 4.1% 5.7%
J f ,f $0 SW
$"'f w
SE 5.7%
6.0% g ;;
zg WIND SPEED TEXT ,
- .c ; LN s
<-i
>24 MPH 19-24 MPH Sgw- SSE
~
7.7% 7'1%
l ft: 13-18 MPH S ~ 8-12 MPH 9.7%
[ 4-7 MPH 39 1-3 MPH
- - :,-. =, .-.-....;...-.-.,-.--.,..,,,.-_..-.,.,...,._.....,
TABLE 11 CLASSIFICATION OF ATMOSPHERIC STABILITY Stability Pasquill Defining Classification Categories Conditions Extremely unstable A -0. 9 0 0<a TS-0. 019 Moderately unstable B -0.019<aTS-0.017 Slightly unstable C' -0.017<aTS-0.015 Neutral D -0.015<aTS-0.005 Slightly stab 1c E. -0. 005<A TS 0. 015 UtJorately stable F 0. 015<a T5 0. 04 0 Extr$E31y stable G 0. 04 0<A TS 0. 900 Invalid e TS-0. 900 or A T>0. 900 AT = temperature difference in Celsius degrees por meter i
40
- a. .~ - - . - n ~ , _~ .-.. , - .. .. _ _ _ - - - _ . - . .~ . _ _ _ . . _ _ _ .
I i
TAttf 12, Page 1 of 7 t
JOINT WIND FREQUENCY DISTRIDUTION DY STABILITY CLASS Data Feriod: January 1, 1992 June 30, 1992 ,
$fA81LifY CLA$1_&
t WIND $ PEED (MPN) At 10 WETEA LEVEL glRECf104 13- 47 8 12 13 18 19 24 324 TOTAL. ;
N 2.00f 00 6.00E 00 1.60E 01 2.40E 01 2.00E 00 0.00E 01 5.00E 01 ,
NNE 0.00E 01 4.00E 00 2.10E 01 1.90E 01 0.00E*01 0.00E 01 4.40E 01 NE 2.00E 00 3.00E 00 9.00E 00 0.00E 01 0.00E 01 0.00E 01 1.40E 01 ENE 0.00E 01 4.00E 00 1.10E 01 1.00E 00 0.00E*01 0.00E 01 1.60E 01 E 2.00E 00 5.00E 00 1.10E 01 1.00E 00 0.00E 01 0.00E 01 1.90t 01 ESE 0.00E 01 4.00E 00- 1.00E 00 0.00fa01 0.00E 01 0.00E*01 5.00E 00 SE 0.00E 01 $s00E 00 2.00E 00 0.00E 01 0.00E-01 0.00E 01 7.00E 00
$$f 1.00E 00 0.00E 01 3.00E 00 0.00E 01 0.00E 01 0.00E 01 4.00E 00
$ 1.00E 00 3.00E 00 8.00E 00 1.50E 01 5.00E 00 0.00E*01 3.20E 01 i
$5W 0.00E 01 1.00E 00 8.00E 00 4.00E 00 5.00E 00 0.00Ea01 1.8DE 01 SW 0.00E 01 3.00E 00 1.00E 00 2.00E 00 1.00E 00 0.00E 01 f.00E 00 W$W 0.00E 01 3.00E 00 4.00E 00 8.00E 00 0.00E 01 1.00E 00 1.60E 01 W 0.00E-01 2.00E 00 1.00E 01 1.40E 01 0.00E 01 1.00E 00 2.70E 01 ONW 1.00E 00 0.00E 01 9.00E 00 1.70E 01 3.00E 00 1.00E 00 3.10f 01
. WW - 1.00E 00 2.00E 00 1.00E 01 1.60E 01 3.00E 00 4.00E 00 3.40E 01 NNW 0.00E-01 11Q2f 00 1.30E 01 3.00E 00 2.00E 00 1.00E 00 .j[iOOE 01 total - 1.00E 01 4.60E 01- 1.37E 02 1.22t 02 2.10E 01 8.00E 03 3.44E 02 Pta10DL OF CALN (HOURS): 0.005 00 WIND SPEED (Mru) At 6 _jffER LEvfL DIRECTION 13 47 8 12 13 18 19 24 >24 TOTAL N 0.00E 01 3.00E 00 1.50E 01 2.10E 01 1.40E 01 1.00E 00 5.40E 01 ,
NNE 1.00E C0' 1.00E 00 1.20E 01 1.70E 01 6.00E 00 0.00E 01 3.70E 01 NE 0.00E 01 - 3.00E 00 4.00E 00 7.00E 00- 0.00E 01 0.00E 01 1.40E 01 ENE 1.00E 00 2.00E 00 7.00E 00 7.00E 00 0,00E-01 0.00E 01 1.70E 01 E 2.00E 00- 4.00E 00 4.00E 00 6.00E 00- 6.00E 00 'O.00E 01 2.20E 01 Est 0.00E*01 1.00E 00 1,00E 00 0.00E 01 0.00E 01 0.00E 01 2.00E 00 SE 1.00E 00 3.00E 00 1.00E 00 1.00E 00 0.00E 01 0.00E 01 6.00E 00 i SSE 1.00E 00 1.00E 00 0.00E 01 3.00E 00 0.00E 01 0.00E-01 5.00E 00
$ .1.00E Ou 2.00E 00 5.00E 00 5.00E 00 1.00E 01 8.00E 00 3.10E 01
$$W 0.00E+di- 1.00E 03 7.00E 00 2.00t 00 3.00E 00 6.00E 00 1.90E 01 SW 0.00E 01 0.00E'01 4.00E 00' .1.00E 00 2.00E 00 0.00E 01 7.00E 00 VSW 0.00E 01 3.00C 00 2.00E 00 1.20E 01 2.00E 00 1.00E 00.. 2.00E 01 W 1.00E 00_ _.2.00E 00 8.00E 00 6.00E 00 6.00E 00 2.00E 00- 2.40E 01 WWW 0.00E 01 0.00E 01 4.00E 00 1.80E 01 5.00f 00 1.00E 00 2.PGE 01 NW 1.00E DO 1.00E 00 5.00E 00 1.30E 01 2.00f 00 6.00E 00 2.80E 01 WNW- 0.00E-01 1.00E 00 '7.00E 00 1.40 01 2.0QE 00 4,00E 00 2.80E 01 TOTAL 9.00E 00 2.80t 01 -8.60E 01 1.33E 03 5.80E 01 2.90E 01 3.43E 02 PERIOOS OF CALM (HOURS): 1.00E 00-41
. . ._ ..__~_ - m _ _ . _ _ . _ _ _ _ _ _ _ _ . . _ _ _ _ . _ _ _ . _ . _ _ . .
?
1ABLE 12, Page 2 of 7 s J0!N1 WIND FREQUENCY 0151RIBU110N BY $1 ABILITY C; Ass f Data Period: Januccy 1. 1992 June 30, 1992 ;
t
$1AB1tl1Y Ctalt 8 WIND $ PEED (MDN) A1 10 METER tEvfL DIRECif0N. 1*3 47 8 12 13 1B 19 24 *24 TOTAL N 2.00E 00 2.00E 00 1.10E 01 1.00E 01 1.00E 00 0.00E 01 2.60E 01 .
NNE- 1.00E 00 1.00E 00 1.10E 01- 9.00E 00 0.00E 01 0.00E 01 2.20E 01 -
NE 0.00E 01 3.00E 00 7.00E 00 2.00E 00 0.00E 01 0.00E*01 1.20E 01 l ENE 0.00E*01 4.00E 00 2.00E 00 0.00E 01 0.00E 01 0.00E 01 6.00E 00 ,
E 0.00E-01 . 3.00E 00 5.00E 00 2.00E 00 0.00E*01 0.00E*01 1.00E 01 j ESE. 0.00E 01 7.00E 00 2.00E 00 0.00E 01 0.00E 01 0.00E 0: 9.00E 00 ,
SE 0.00E 01 1.00E 00 5.00E 00 0.00E 01 0.00E 01 0.00E-01 6.00E 00 55E 0.00E 01 2.00E 00 1.00E 00 0.00E 01 0.00E 01 0.00E-01 3.00E 00 ;
-$ 2.00E 00 2.00E 00 7.000 00 5.00E 00 0.CJE*01 0.00E 01 1.ddE 01
- 9tW 0.00E 01 i.00E 00 2.00E 00 2.00E 00 1.00E 00 0.00E 01 7.00E 00
$W 1.00E 00- 2.0DE 00 1.00E 00 3.00E 00 0.00E 01 0.00E 01 7.00E 00
/$W ; 0.00E+01 1.00E 00 -2.00E 00 0.00E 01 1.00E 00 0.00E 01 4.00E 00
-W 1.00E 00 1.00E 00 4.001 00 8.00E 00 0.00!*01 0.00E 01 1.40E 01 WNW - 0.00E 01 2.00E 00 4.00E 00 2.00E 00 1.0DE 00 0.00E*01 9.00E 00 NW .0.00E 01 3.00E 00 2.00E 00 3.00E 00 2.00E 00 1.00E 00 1.10E 01 i NNW 0.00E 01 3.00E 00 6.00E 00 6.00E 00 0.00E 01 0.00E 01 1.50E 01 TOTAL 7.00E 00 3.90E 01 7.20E 01 5.20E 01 6.00E 00 1.00E 00 1.77E 02 PERIODS OF CALM (HOURS): 0.00E 01 i WIND $ PEED (MPH) At 60 METER LEyLL DIRECTION '13 47 6 12 13 18 19 ?4 >24 101 At W 1.00E 00 1.00E 00 1.10E 01 1.10E 01 5.00E 00. 0.00E 01 .2.90E 01 NNE 0.00E 01 2.00E 00 7.00E 00 9.00E 00 2.00E 00 0.00E 01 2.00E 01 NE 0.00E 01 2.00E 00 3.00E 00 $.00E 00 0.00E 01 0.00E 1.00E 01 ENE 0.00E 01 2.00E 00 4.00E 00 0.00E 01 3.00E 00 0.00E-01 9.00E 00 E 0.00E 01 2.00E 00 2.00E 00- 1.00E 00 3.00E 00 0.00E 01 8.00E 00 Est- .0.00E*01 7.00E 00 2.00E 00 1.00E 00 0.00E 01 0.00E 01 1.00E 01 SE 0.00E*01 3.00E 00 1.00E 00 0.00E 01 0.00E 01 0.00E 01 4.00E 00 SSE' O.00E*01 1.00E 00 1.00E 00 0.00E 01 0.00E 01' O.00E 01 2.00E 00
$- 2.00E 00 2.00E 00 1.00E 00 9.00E 00 3.00E 00 1.00E 00 1.80E 01
-S$W 1.00E 00 2.00E 00 1.00E 00- 2.00E 00 2.00E 00 1.00E 00 9.00E 00 sw - 0.00E 01 - 2.00E 00 0.00E 01' 2.00E 00 .1.00E 00 0.00E 01 5.00E 00 VSW 0.00E 01 0.00E 01 -4,00E 00- 1.00E 00-- - 0.00E 01 0.00E 01 -5.00E 00 W 0.00E 01 - 2.00E.00 2.00E 00 5.00E 00- 3.00E 00 0.00E+01 1.20E 01 WNW 1.00E 00- 2.00E 00. -3.00E 00 2.00E 00 0.00E 01 1.00E. 00 9.00E 00 NV 0.00E 01 2.00E 00 1.00E 00 2.00E 00 1.00E 00 3.00E 00 9.00E 00 NNW 1.00E 00 4.00E 00 6.00E OQ, 4.00E 00 2.00E 00 1.00E 00 1.80E 01 TOTAL 6.00E 00 3.60E 01 4.90E 01 5.40E 01- 2.50E 01 7.00E 00 1.77E 02 -
PERICOS OF CALM (HOURS):~ 0.00E 01 1
42 t
a#- >-,n ..,p- 3-%c,e,,- ,,,..w
._.. _ m. __. _. _ __.. . _.~. _ _ _ _ _._._ - . _ _ _ .. - _ . _ _ . _ . _ _ _ _ _ . . _ . _ _ -
TABit 12, Page 3 of 7 l
JOINT WIND FREQUthCT Ol$1RIBUil0N BY $1ABILITT CLASS Data Period: January 1,1992 June 30,1992 STABILITT Cl*$5 C WIND SPEED (MPH) At 10 METER LEVEL i
QefeitoN 13 47 B 12 13 18 19 24 >24 TOTAL N 1.00E 00 4.00E 00 1.10E 01 9.00E 00 3.00E 00 1.00E 00 2.90E 01 NNE 0.00E 01 4.00E 00- 8.00E 00 7.00E 00 1.00E 00 0.00E 01 2.00E 01 NE 1.00E 00 7.00E 00- 1.00E 00 0.00E 01 0.00E 01 0.00E 01 9.00E 00 ENE 0.00E 01 5.00E 00 8.00E 00 1.00E 00 0.00E 01 0.00E 01 1.40E 01 I t 0.00E 01 7.00E 00 3.00E 00 0.00E 01 0.00E 01 0.00E 01 1.00E 01 ESE 1.00E 00 6.00E 00 6.00E 00 0.00E 01 0.00E 01 0.00E 01 1.30E 01 SE 2.00E 00 1.10E 01 8.00E 00 0.00E 01 0.00E 01 0.00E 01 2.10E 01 51E 2.00E 00 - 1.00E 00 7.00E 00 0.00E 01 0.00E 01 0.00E 01 1.00E 01 8 1.00E 00 8.00E 00 1.10E 01 6.00E 00 2.00E 00 0.00E 01 2.80E 01 S$W 0.00E 01' 4.00E 00 7.00E 00 5.00E 00 7.00E 00 0.00E 01 2.30E 01 SW 0.00E 01 2.00E 00 4.00E 00 4.00E 00 0.00E 01 0.00E 01 1.00E 01 VSW 0.00E 01 1.00E 00 6.00E 00 7.00E 00 1.00E 00 0.00E 01 1.50E 01 W 0.00E 01- . 5.00E 00 7.00E 00 2.00E 00 0.00E 01 0.00E 01 1.40E 01 WNW 0.00E 01 4.00E 00 3.00E 00 3.00E 00 2.00E 00 0.00E 01 1.20E 01 NW 2.00E 00 - 3.00E 00- 1.10E 01 1.10E 01 2.00E 00 0.00E 01 2.90E 01 1 NNW 0.00E 01 1.00E 00 6.00E 00 1.20E 01 2.00E 00 0.00E 01 2.10E 01 101AL 1.00E 01 /.30E 01 1.07E 02 6.70E 01 2.00E 01 1.00E 00 2.78E 02 i
PERIODS OF CALM (HOURS): 0.00E 01 VIND $ PEED iMPO Af 60 NE1[R LEVEL I
DIREtf10N 13 47- 8 12 13 18 19 24 >24 total N 0.00E*01 3.00E 00 9.00E 00 9.00E 00 7.00E 00 3.00E 00 3.10E 01
- . NNE 1.00E 00 2.00E 00 6.00E 00 6.00E 00 3.00E 00 1.00E 00 1.90E 01 kE 1.00E 00 2.00E On 5.00E 00 1.00E 00 0.00E 01 0.00E 01 9.00E 00 l ENE 0.00E 01 3.00E 00= 4.00E 00 6.00E 00 -3.00E 00 0.00E 01 1.60E 01 l E 0.00E 01 3.00E 00 5.00E 00 2.00E 00 0.00E 01 0.00E 01 1.00E 01 ESE 2.00E 00 5.00E 00 5.00E 00 1.00E 00 0.00E 01 0.00E 01 1.30E 01 SE - 1.00E 00 9.00E 00 6.00E 00 1.00E 00 0.00E 01 0.00E 01 1.70E 01
$$f 1.00E 00 3.00E C0 4.00E 00- 5.00E 00- 0.00E IO1 0.00E 01 1.30E 01
$ 1.00E 00 3.00E 00 5.00E 00 '1.10E 01 3.00E 00 -3.00E 00 2.60E 01 )
- ssw 1.00E 00' 4.00E 00- 5.00E 00 4.00E 00 2.00E 00 9,00E 00 2.50E 01 I
SV 0.00E 01 2,00E 00 2.00E 00 : 4.00E 00 2.00E 00 0.00E 01 1.00E 01 Vsv 0.00E 01 0.00E 01 6.00E 00 5.00E 00 4.00E 00 0.00E-01 1.50E 01 W 0.00E 01 4.00E 00 4.00E 00 4.00E 00 2.00E 00 0.00E 01 1.40E 01 WNW 1.00E 00 5.00E 00 1.00E 00 0.00E+01 2.00E 00 0.00E 01 9.00E 00 NW 0.00E 01 1.00E 00 1.10E 01 1.20E 01 2.00E 00 2.00E 00 2.80E 01 !
WW 1.00E 00 0@E 01 6.00E 00 1.00E 01 5.00E 00 1.00E 00 2.30E 01 TOTAL 1.00E 01 4.90E 01 8.40E 01 8.10E 01 3.50E 01 1.90E Q1 2.78E 02 PERIOOS OF CALM (HOURS): 0.00E 01
!~
43 V
EY
3 TABLE 12. Page 4 of 7 JOINT WIND FREDUENCf OltfRIBUTION BT STABILif f CLA$$
Data Periodt January 1,1992 June 30,1992
$1ABILI11 CLAS$ D WIND $PfED (McH) At 10 Mitta (Evit glREct10N 13 47 8 12 13 19 19 24 >24 70TAL N 9.00E 00 3.50E 01 6.00E 01 3.90E 01 8.00E 00 0.00E 01 1.51E 02 WWE 3.00E 00 2.70E 01 3.70E 01 2.20E 01 1.00E 00 0.00E 01 9.00E 01 NE 9.00E 00 2.$0E 01 5.90E 01 3.20E 01 8.00E 00 0.00E-01 1.33E 02 ENE 1.00E 01 4.20E 01 5.60E 01 4.00E 01 0.00E 01 0.00E 01 1.12E 02 E 1.00E 01 5.70E 01 4.00E 01 2.00E 00 0.00E 01 0.00E 01 1.09E 02 ESE 1.90E 01 6.80E 01 4.50E 01 1.00E 00 -0.00E 01 0.00E 01 1.337 U2
$E 1.70E 01 5.70E 01 4.70E 01 1.00E 01 0.00E 01 0.00E 01 1.31E 02
$$E 2.20E 01 3.50E 01 4.90E 01 1.50E 01 0.00E 01 0.00E 01 1.21t 02
$ 1.80E 01 3.30E 01. 5.10E 01 3.00E 01 1.00E 00 0.00E 01 1.33E 02
$$W 1.10E 01 2.10E 01 4.50E 01 3.60E 01 7,00E 00 1.00E 00 1.22E 01
$V 6.00E 00 3.10E 01 4.00E 01 2.40E 01 3.00E 00 0.00E 01 1.04E 02 VSW 5.00E 06 1.60E 01 2.60E 01 3.10E 01 0.00E 01 0.00E 01 7.80E 01 W 2.00E 00 2.$0E 01 6.20E 01 5.70E 01 6.00E 00 2.00E 00 1.54E 02 DVNW 5.00E 00 1.70E 01 4.40E 01 3.90E 01 1.60E 01 4.00E 00 1.25E 02 NW 6.00L 00 3.40E 01 7.00E 01 4.20E 01 0.00E 01 0.00E 01 1.52E 02 NwV 5.00E 00 3.90E 01 6.20E 01 3.50E 01 1.10E 01 1.00E 00 .53E 02 total 1.57E 02 5.62E 02 7.93E 02 4.19E 02 6.102 01 8.00E 00 2.00E 03 PERIOD $ OF CALM (HOURS): 3.00E 00 VIND SPEED (MPN) AT 60 METER LEVFL DIRECTION 13 47 8 12 13 18 19 24 324 total-N 5.00E 00 2.70E 01 5.20E 01 5.80E 01 2.00E 01 8.00E 00 1.70E 02 NNE- 4.005 00 1.10E 01 2.60E 01 3.40E 01 1.20E 01 3.00E 00 9.00E 01 NE 5.00E 00 9.00E 00 2.40E 01- 3.70E 01 4.20E 01 1.20E 01 1.29E 02 ENE 3.00E 00 1.50E 01 3.30E 01 4.40E 01 1.00E 01 1.00E 00 1.06E 02 E 6.00E 00 2.10E 01 4.70E 01 3.80E 01 4.00E 00 1.00E 00 1.17E 02 ESE 9.00E 00 4.90E 01 4.30F 01 1.10E 01 0.00E 01 0.00E*01 1.12E 02 SE 1.6st 01 2.90E 01 3.00E 01 3.00E 01 7.00E 00 1.00E 00 1.13E 02
$$E -2.10E 01 2.30E 01 2.80E 01 4.50E 01 1.60E 01 .1.00E 01 1.43E 02 -
$ 1.90E 01 3.00E 01 2.403 01- 4.20E 01 3.00L 01 1.50E 01 1.60E 02
$$W !.00E 00 1.60E 01 2.60E 01 3.90E 01 1.40E 01 1.30E 01 1.15E 02
$W 2.00E 00 1.90E 01 3.10E 01 3.90E 01 1.50E 01 2.00E 00 1.08E 02 USW = 2.00E 00 1.00E 01 2.00E 01 2.40E 01 2.10E 01 0.00E 01 7./0E 01 W 3,00E 00- 1.00E 01 3.50E 01 4.50E 01 2.80E 01 9.00E 00 1.30E 02
- WNW 3.00E 00 ' 6.00E 00 2.60E 01 4.10E 01 1.20E 01' 1.00E 01 9.80E 01 WW 2.00E 00 2.00E 01 5.90E 01 6.40E 01 1.90E 01 7.00E 00 1.71E 02 NvV 1.20E 01 1.90E 01 6.60E 01 3.50E 01 2.00E 01 9.00E 00 1.61E 02 TOTAL 1.19E 02 3.14E 02 5.70E 02. 6.26E 02 2.70E 04 1.01E 02 - 2.00E 03 PERIDOS OF CALM (HOURS): 3.00E 00 44 <
i 1ABLE 12, Page 5 of 7 J0lWT WIND ftEQUENCY DISTRIBUTION SY STAB. 111 "**1 Data Period: January 1, 1992 June 30, 14.,
jfillitTV ELAts E VlWD SPitD (MPw) Af 10 METER LEyLi DIRECTION 13 47 8 12 13 10 10 24 >24 total N 5.00E 00 2.00E 01 1.40E 01 1.00E 00 0.00E 01 0.00E 01 4.00E 01
- kWE 7.00E 00 1.80E 01 9.00E 00 1.00E 00 0.00E 01 0.00E 01 3.50E 01 ht 1.20E 01 3.20E L1 1.80E 01 0.00E 01 0.00E 01 0.00E 01 6.20E 01 >
EWE 7.00E 00 3.20E 01 1.00E 01 0.00E 01 0.00E 01 0.00E 01 4.90E 01 E 1.00E 01 3.30E 01 4.00E 00 0.00E 01 0.00E 01 0.00E 01 4.70E 01 ESE 1.50E 01 4.20E 01 1.00E 00 0.00E*01 0.00E 01 0.00E 01 5.80E 01
$E 1.70E 01 4.50E 01 2.20E 01 0.00E 01 0.00E 01 0.00E 01 8.40E 01
$5E 1.10E 01 5.20E 01 3.20E 01 2.00E 00 0.00E 01 0.00E 01 9.70E 01 S 2.00E 00 3.10E 01 5.20E 01 1.90E 01 0.00E 01 0.00E 01 1.04E 02 SSW 1.00E 00 4.00E 01 6.40E 01 1.70E 01 1.00E 00 0.00E 01 1.23E 02
$W 1.00E 00 2.50E 01 3.50E 01 8.00E 00 1.00E 00 0.00E 01 7.00E 01 WSW 2.00E 00 1.60E 01 2.20E 01 $.00E 00 0.00E 01 0.00E 01 4.50E 01 W 3.00E 00 1.20E 01 8.00E 00 1.00E 00 0.00E 01 0.00E 01 2.40E 01 WWW 4.00E 00 1.40E 01 8.00E 00 5.00E 00 0.00E 01 0.00E 01 3.10E 01 NW 5.00E 00 2.00E 01 2.00E 00 1.00E 00 0.00E 01 0.00E*01 2.80E 01
- WWW - 3.00E 00 1.40E 01 5.00E 00 1.00E 00 0.00E-01 0.00E 01 2.30E 01
- TOTAL 1.05E 02 4.46E 02 3.06E 02 6.10E 01 2. 00E 00 0.00E 01 9.20E 02 PERIOOS OF CALM (HDURS): 3.00E 00 WIND SPEED (MPM) At 60 METER LEVEL DIRECTION 1+3 4-7 8 12 13 18 19 24 >24 TOTAL N 0.00E 01 4.00E 00 - 2.00E 01 1.10E 01 1.00E 00 0.00E 01 - 3.60E 01 kNE 1.00E 00 8.00E 00 1.20E 01 1.90E 01 3.00E 00 0.00E 01 4.30E 01 NE 0.00E 01 8.00E 00 1.40E 01 2.60E 01 3.00E 00 0.00E 01 $.10E 01 ENE - 1.00E 00 5.00E 00 1.40E 01 2.70E 01 1.00E 00 0.00E 01 5.30E 01 E 3.00E 00 4.00E 00 1.60E 01 2.00E 01 0.00E 01 0.00E 01 4.30E 01-
.ESE- 2.00E 00 1.70E 01 3.50E 01 1.00E 00 0.00E 01 0.00E 01 5.50E 01 SE 5.00E 00 1.20E 01 3.00E 01 2.00E 01 7.00E 00 0.00E 01 7.40E 01
^$5E 4.00E 00 -4.00E 00 2.500 01 5.20E 01 1.00E 01 0.00E 01 9.50E 01 5 3.006 00 9.00E 00 2.50E 01 6.20E 01 2.50E 01 6.00E 00 1.30E 02 SSW 1.00E 00 5.00E 00 2.10E 01 4.90E 01 3.40E 01 6.00E 00 1.16E 02 <
SW 0.00E 01 3.00E.00- 1.50E 01 5.10F 01 1.30E 01 4.00E 00 8.60E 01 WSW 1.00E 00 2.00E 00 1'10E
. 01 1.90E 01 3.00E 00 0.00E 01 3.60E 01 W- 1.00E.00 2.00E 00 1.30E 01 6.00E 00 2.00E 00 0.00E 01 2.40E 01 WNW. 1.00E 00 5.00E 00 7.00E to- 6.00E 00 -3.00E 00 0.00E 01 2.20E 01 NW 0.00E 01- 4.00E 00 1.90E 01 6.00E 00 1.00E 00 0.00E 01 -3.00E 01 WWW 1.00E 00 6.00E 00 1.30E 01 7.00E 00 1.00E 00 0.00E 01 2.80E 01 101AL 2.40E 01 9.80E 01 2.95E 02 3.82E 02 1.07E 02 1.60E 01 9.22E 02.
-PERIDOS OF CALM (HOURS): 1.00E 00 45
r 1ABLE 12, Page 6 of 7 JOINT WIND FREQUENCY DISTRIDUTION DY STABILITY CLASS Data Period: January 1, 1992 June 30, 1992 ITABillTV CL ASS f WIND $>EED (MPW) AT 10 METER LEvfL PIRECff0N 13 47 8 12 13 15 19 24 >24 TOTAL __
N 0.00E 01 0.00E 00 4.00E 00 0.00E 01 0.00E-01 0.00E 01 4.00E 00 NNE 8.00E 00 1.10E 01 1.00E 00 0.00E 01 0.00E 01 0.00E 01 2.00E 01 NE 7.00E 00 1.90E 01 0.00E 01 0.00E*01 0.00t 01 0.00E 01 2.60E 01 Eht 1.20E 01 1.40E 01 1.00E 00 0.00E 01 0.00E 01 0.00E 01 2.70E 01 L E 1.30E 01 1.4'0E 01 0.00E 01 0.00E-01 0.00E 01 0.00E 01 3.20E 01 ESE 1.60E 01 1.20E 01 0.00E 01 0.00E 01 0.00E 01 0.00E 01 2.80E 01 SE 1.20E 01 1.00E 01 2.00E 00 0.00t 01 0.00E 01 0.00E 01 2.40E 01
$$E 3.00E 00 2.20E 01 4.00E 00 0,00E 01 0.00E 01 0.00E 01 2.90E 01 S 3.00E 00 2.00E 01 2.00E 00 0.00E 01 0.00E 01 0.00E 01 2.50E 01 SSW 5.00E 50 1.30E 01 1.50E 01 0.00E 01 0.00E 01 0.00E 01 3.30E 01 SW 1.00E 00 1.20E 01 7.00E 00 0.00E 01 0.00E*01 0.00E 01 2.00E 01 WSW 1.00E 00 7.00E 00 1.00E 00 0.00E 01 0.00E 01 0.00E 01 9.00E 00 W 2.00E 00 5.00E 00 1.00E 00 1.00E 00 0.00E-01 0.00E-01 9.00E CO WNW ' 00E 00
. $.00E 00 0.00L 01 0.00E 01 0.00E 01 0.00E 01 8.00E 00 NV 5.00E 00 2.00F 01 0.00E 01 0.00E*01 0.00E 01 0.00E 01 2.50t 01 '
WNW 3.00E 00 2.00E 00 0.00E 01 0.00E 01 0.00E 01 0.00E 01 5.00E 00 TOTAL 9.40E 01 1.91E 02 3.60E 01 1.00E 00 0.00E 01 0.00E 01 3.24E 02 PERIDOS OF CALM ' HOURI): 1.00E 00 VIND MPEED (MPH) AT 60 NETER L EVEL DIRECTION 13 47 8 12 13 18 19 24 324 TOTAt W 2.00E 00 1.00E 00 2.00E 00 3.00E 00 1.00E 00 0.00E 01 9.00E 00 NNE -1.00E 00 2.00E 00 6.00E 00 5.00E 00 0.00E 01 0.00E 01 1.40E 01 NE 0.00E 01 1.00E 00 6.00E 00 6.00E 00 0.00E 01 0.00E 01 1.30E 01 ENE 0.00E 01 1.00E 00 6.00E 00 1.30E 01 1.00E 00 0.00E 01 2.10E 01 E 0.00E 01 4.00E 00 1.80s 01 6.00E 00 4.00E 00 0.00E 01 3.20E 01 ESE .1.00E 00 1.00E 01 1.60E 01 2.00E 00 0.00E 01 0.00E*01 2.90E 01 SE 0.00E-01 4.00E 00 1.10E 01- - 4.00E 00 4.00E 00 0.00E 01 2.30E 01 SSE 2.00E 00 5.00E 00 1.60E 01 1.00E 01 0.00E 01 0.00E 01 3.30E 01 S 2.00E 00 3.00E 00 -9.00E 00 2.30E 01 0.00E 01 0.00E 01 3.70E 01 SSW 1.00E 00 4.00E 00 6.00E 00 1,90E 01 4.00F 00 0.00E 01 3.40E 01 l SW 0.00E 01 _2.00E 00 4.00E 00 1.40E 01 3.00E 00 0.00E 01 2.30E 01 VSW 0.00E 01 0.00E 01 4.00E 00 6.00E 00 0.00E 01 0.00E 01 1.00E 01 W 1.00E C3 1.00E 00 4.00E'00 2.00E 00 1.00E 00 0.00E 01 9.00E 00 VNW 1.00E'00' 1.00E 00 5.00E 00 2.00E 00 1.00E 00 0.00E-01 1.00E 01 NW 1.00E 00 3.00E 00- 3.00E 00 4,00E 00 0.00E 01 0.00E 01 1.10E 01 l NNV 0.00E 01 1.00E 00 1.20E 01 3.00E 00 0.00E 01 0.00E 01 1.60E 01 1.2": 02 l
TOTAL 1.20E 01 4.30E 01 1.22E 02 1.90E 01 '0.00E 01 3.24E 02 PERIDOS OF CALM (HOURS): 1.00E 00 46
.. -. - . - - - ~ . . - - - . . , -
TABLE 12, Page 7 of 7 JOINT WIND FREQUENCY DISTRIDUTION DY STADILITY CLAS8 Data Periodt January 1,1992 June 30,1992
$18Bftlff class C WIND $PfED (WPN) A1 10 #f f f R L EVEL gjl[CTION 13 47 8 12 13 18 19 24 >P4 TOTAL l l
N 9.00E 00 1.00E 00 0.00E . 0.00E 01 0.00E 01 0.00E 01 1.00E 01 NNE 1.10E 01 1.30E 01 0.00E 01 0.00E 01 0.00E 01 0.00E 01 2.40E 01 NE 1.50E 01 2.10E 01 0.00E 01 0.00E 01 0.00E 01 0.00E 01 3.60E 01 ENE 1.20E 01 4.00E 00 0.00E 01 0.00E 01 0.00E 01 0.00E 01 1.60E 01 E 2.00E 00 2.00E 00 0.00E 01 0.00E 01 0.00E 01 0.00E 01 4.00E 00 ESE 4.00E 00 1.00E 00 0.00E 01 0.00E 01 0.00E 01 0.00E 01 5.00E 00
$E 4.00E 00 4.00E 00 0.00E 01 0.00E 01 0.00E 01 0.00E 01 8.00E 00 !
$$E 2.00E 00 4.00E 00 0.00E 01 0.00E*01 0.00E 01 0.00E 01 6.00E 00
$ 0.00E 01 5.00E 00 0.00E-01 0.00E*01 0.00E 01 0.00E 01 5.00E 00
$$W 7.00E 00 7.00E 00 0.00E 01 0.00E*01 0.00E 01 0.00E 01 1.40E 01 SW 2.00E 00 4.00E 00 0.00E 01 0.00E 01 0.00E 01 0.00E 01 6.00E 00 WSW 3.00E 00 4.00E 00 0.00E 01 0.00E 01 0.00E 01 0.00E 01 7.00E 00 W 2.00E 00 3.00E 00 0.00E 01 0.00E 01 0.00E 01 0.00E 01 5.00E 00 VNW 7.00E 00 2.00E 00 0.00E 01 0.00E 01 0.00E 01 0.00E 01 9.00E 00 NW 5.00E 00 5.00E 00 0.00E 01 0.00E 01 0.00E 01 0.00E 01 1.00E 01 NNV 4.00E 00 0.00E 01 0 00E 01 0.00E 01 0.001-01 0.00E 01 4.00E 00 10fAL 8.90E 01 8.00E 01 0.00E 01 0.00E 01 0.00E 01 0.00E 01 1.67E 02 PER100$ OF CALM (HOURS): 1.00E 00 L VIND SPf E0 (MPN) AT 60 METER LEV 1L DIRf0flDN 13 47 8 12 13 18 19 24. >P4 TOTAL N 3.00E 00 2.00E 00 1.00t 00 0.00E 01 0.00E 01 0.00E 01 6.00E 00 NNE 0.00E 01 2.00E 00 2.00E 00 1.00E 00 0.00E 01 0.00E 01 5.00E 00
- NE 3.00E 00 3.00E 00 , .00E 00 5.00E 00 1.00E 00 0.00E-01 1.60E 01 EWE 1.00E 00 4.00E 00 6.00E 00 1.00E 01 0. DOE 01 0.00E-01 2.10E 01 l E 1.00E 00 5.00E 00 1.10E 01 3.00E 00 0.00E 01 0.00E-01 2.00E 01 !
ESE 1.00E 00 8.00E 00 1.10E 01 0.00E 01 0.00E 01 0.00E ~01 2.00E 01 SE 1.00E 00 1.00E 00 2.00E 00 1.00E 00 0.00E 01 0,00E 01 5.00E 00 SSE 1.00E 00 4.00E 00 4.00E 00 3.00E 00 0.00E 01 0.00E-01 1.20E 01 S 0.00E 01 1.00E 00 3.00E 00- 4.00E 00 0.00E 01 0.00E 01 8.00E 00 i SSW 0.00E 01 0.00E 01 1.00E 00 5.00E 00 0.00E 01 0.'0E 01 6.00E 00 SW 2.00E 00- 3.00E 00 6.00E 00 4.00E 00 0.00E U1 0.00E 01 1.50E 01 WSW -0.00E 01 3.00E 00 5.00E 00' 2.00E 00 0.00E*01 0.00E 01 1.00E 01 W 0.00E 01 1.00E 00 2.00E 00 2.00E 00 0.00E 01 0.00E 01 5.00E 00 WNW 2.00E 00 1.00E 00 3.00E 00 1.00E 00 0.00E 01 0.00E 01 7.00E 00 NW 0.00E 01 0.00E-01 2.00E 00 3.00E 00' O.00E-U1 0.00E 01 5.00E 00 NwV- 1.00E 00 3.00E 00 4200E 00 0.00E 01 0.00E 01 0.00E 01 8.00E 00 l.'
10TAL 1.60E 01- 4.10E 01 6.70E 01 4.40E 01 1.00E 00 0.00E 01. 1.69E 02 PERIODS OF CALM (HOURS): 1.00E 00 47 i
1
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SECTION 6 DOSE MEASUREMENTS AND ASSESSMENTS L
9
i TABLE 13 MAXIMUM
- OFFBITE DOSES AND DOSE COMMITMENTS TO MEMBERS OF THE PUBLIC Data Period: January 1,-1992 - June 30, 1992 Source 1st Qtr. 2nd Qtr. 3rd Qtr. 4th Qtr.
A. Waterborne Effluents (mrem):
Organ 3.34E-02 1 4.64E-03 1 Total Body 3.32E-03 2 4.54E-04 2 B. Airborne
- Effluents
- 1. Iodines and particulates (mrom):
Organ 4.58E-04 3 2.11E-04 4 Total Body 1.69E-05 5 2.33E-05 6 2, Noble Gases (mrad):
Gamma 0.00E+00 7.40E-05 7 l Beta 0.00E+00 fi.46E-05 7
~
C. Direct Radiation (mrem): _0.00E+00 0.00E+00 THERE ARE NO OTHER URANIUM FUEL CYCLE FACILITIES WITHIN 8 KM OF CPS
- " Maximum" means the largest fraction of the corresponding Appendix I dose design objective.
- The numbered footnotes on the following page briefly explain how each maximum dose was calculated, including the organ and predominant pathway (s).
48
Footnotes for Table 13
- 1. Dose to the adult ~ gastrointestinal tract and lower large
-intestine _(GI-LLI) by the fish pathway. Calculated using methodology contained.in the CPS Offsite Dose Calculation Manual (ODCM).
2.- Dose to the-adult total body by the fish pathway. Calculated
-using nethodology contained in the CPS ODCM.
- 3. Dose to the infant thyroid via the inhalation, cow milk, and ground-plane pathways. Calculated at 4.5 miles North using methodology-contained in the CPS ODCM.
- 4. Dose to the infant thyroid via the inhalation, cow milk and ground-plane pathways. Calculated at 4.5 miles West Southwest
-using methodology contained in the CPS ODCM.
- 5. Dose to the-infant total body via the inhalation. cow milk and grcund-plane pathways. Calculated at 4.5 miles North Northeast using methodology contained in the CPS ODCM.
- 6. ' Dose to the infant total body via the inhalation, cow milk and ground-plane pathways. Calculated at 4.5 miles' South Southwest using methodology contained in the CPS UDCM.
- 7. Dose to total body and skin. Calculated at 4.5 miles North using methodology contained in the CPS ODCM.
&r 49
DOSES TO MEMBERS OF__THE PUBLIC WITHIN THE SITE DOUNDARY requires that the CPS Offsite Dose Calculation Manual Semiannual Radioactive Effluent Release Report section 7.2 include an assessment of the radiation doses from radioactive liquids and gaseous effluents to MEMBERS OF THE PUBLIC The meteorological due to their conditior.. activities concurrent inside the SITE BOUNDARY. in gaseous with effluentsthe time shall of berelease used forofdetermining radioactivethe materials gaseous pathway doses.
Within the CPS site boundary there are seven areas which are open (see to members o'J the public as identified by CPS ODCM Table 3.4-4 Figure 7):
A road at 0.495 kilometers (0.3 miles) in the SE sector Agricultural acreage at 1.372 kilometers (0.9 miles) in the SSW sector
- A portion of Clinton Lake at 0.335 kilometers (0.2 miles) in the NW sector 1.287
- The Department of Conservation Recreation Area at kilometers (0.8 miles) in the ESE sector
- A residence at 1.219 kilometers (0.8 miles) in the SW sector
- A residence at 2.414 kilometers (1.5 miles) in the WSW sector A residence at 2.736 kilometers (1.7 miles) in the SSE sector At all of the above locations, the plume, inhalation and ground- No other plane exposure pathways are used for dose calculations.
exposure Census.
pathways were identified by the 1991 Annual Land UseAll d contained in the CPS ODCM The calculated doses to members through of 20 theshow publicthe residing in greatest organ of the seven released sectors burden listed in Tables as the liver. 14This liver burden was due to Cs-138 while operating the CPS off gas system in the by-pass mode while at power. Table 2 does not identify Cs-138 as a particulate released Off gas because of Cs-138's short half life (t1\2 = 32.2 minutes).
by-pass mode operation is allowed by plant procedures, a off gas system it became necessary for a five day period due to a problem with establishing normal flow through the charcoal adsorbers.
50
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TABLE 14 CALCULATED DOSES TO MEMBERS OF THE PUBLIC DURING USE OF THE ROAD IN THE SOUTHEAST SECTOR WITHIN THE CPS SITE DOUNDARY Data Period: -January 1, 1992 - June 30, 1992 Excosure Pathway Orcans pose (mren) plume
- total body 2.04E-05 skin 4.38E-05 ground plane
- total body 1.56E-05 skin 1.81E-05 inhalation; four highest organ doses:
teen liver 3.99E-06 child liver 3.74E-06 adult liver 3.38E-06 teen kidney 3.05E-06
- Doses via these pathways are not dependent upon age-group.
52
- - ~ ~ . . .
TABLE 15 CALCULATED DOSES TO MEMBERS OF THE PUBLIC DURING USE OF THE AGRICULTURAL ACREAGE IN THE SOUTH-SOUTHWEST SECTOR WITHIN THE CPS SITE BOUNDARY Data Period: January 1, 1992 - June 30, 1992 Exposure Pathway Orcans D_ose (mrem) plume
- total body 3.10E-05 skin 6.68E-05 ground plane
- total body 2.66E-05 skin 3.09E-05 inhalation; four highest organ doses:
teen liver 4.16E-06 child liver 3.98E-06 infant liver 3.38E-06 adult liver 3.29E-06
- Doses via these pathways are not dependent upon age-group.
53
TABLE 16 CALCULATED DOSES TO MEMBERS OF THE PUBLIC DURING USE OF CLINTON LAKE IN THE NORTHWEST BECTOR WITHIN THE CPS SITE BOUNDARY Data Period: -January 1, 1992 - June 30, 1992 Exposure Pathway Orcans Dose (mremi plume
- total body 7.21E-04 skin 1.55E-03 ground plane
- total body 2.24E-04 skin 2.59E-04 inhalation; four highest organ doses:
teen liver 9.24E-05 child liver 8.93E-05 infant liver 7.88E-05 adult liver 7.07E-05
- Doses via these pathways are not' dependent upon age-group.
54
TABLE 17 CALCULATED DOSES TO MEMBERS OF THE PUBLIC DUR1NG USE OF THE DEPARTMENT OF CONSERVATION RECREATION AREA IN THE EAST-SOUTHEAST SECTOR WITHIN THE CPS SITE BOUNDARY Data Period: January 1, 1992 - June 30, 1992 Exoosure Pathway Orcans Dose (mreml plume
- total body 2.72E-05 skin 5.83E-05 ground plane
- total body 2.55E-05 skin 2.95E-05 inhalation; four highest organ doses:
teen liver 3.37E-06 child liver 3.25E-06 infant liver 2.8'/S-06 adult-liver 2.58E-06
- Doses via these pathways are not dependent upon age group.
55
i TABLE 18 CALCULATED DOSES FOR THE RESIDENTS IN THE SOUTHWEST SECTOR WITHIN THE CPS SITE BOUNDARY Data Period: January 1, 1992 - June 30,1992 Exposure Pathway Orcans Dose (mremi plume
- total body 4.32E-04 skin 9.28E-04 ground plane
- total body 2.15E-04 skin 2.50E-04 inhalation; four highest organ doses:
teen liver 6.45E-05 child liver 6.12E-05 adult liver 5.24E-05 infant liver 5.05E-05
- Doses via these pathways are not dependent upon age-group.
TABLE 19 !
CALCULATED DOSOS FOR THE RESIDENTS IN THE WEST-SOUTHWEST SECTOR WITHIN THE, CPS SITE BOUNDARY Data Period: January 1, 1992 - June 30, 1992 Exocsure P3thway Oraans Dose (nrem) plume
- total body 1.75E-04 skin 3.75E-04 grous.d plane
- total body 6.61E-05 skin 7.69E-05 inhalation; feur highest organ doses:
teen liver 2.18E child liver. 2.10E-05 infant liver 1."1E-OS adult liver 1./1E-05
-i
- Doses via these pathways are not dependent upon
- age-group.
l' i-l-
l.
57
TABLE 20 CALCULATED DOSES FOR THE RESIDENTS IN THE SOUTH-SOUTHEAST SECTOR WITHIN THE CPS SITE BOUNDARY Data Period: January 1, 1992 - June 30, 1992 Exoosure Pathway Orcans Dose (mrem) plume
- total body 4.04E-05 skin 8.69E-05 ground plane
- total body 5.61E-05 skin 6.55E-05 inhalation; four highest organ doses:
teen liver 9.21E-06 child liver 8.37E-06 adult liver 8.05E-06 teen kidney 7.43E-06
- Doses via these pathways are not dependent upon L age-group.
I l-i-
58
SECTION 7 CHANGES TO THE OFFSITE DOSE.
- CALCULATION MANUAL
CHANGES TO THE OFFSITE _ QQ1E_, CALCULATION MANUAL In accordance with CPS Technical Specification 6.14 and ODCM-section 7.2, changes to the CPS ODCM shall be - eported as a part of or concurrent with the Semiannual Radioactive Effluent Release Report.
The CPS ODCM was not revised during this reporting period.
i I-i t
59
I I
SECTION 8 0FFSITE DOSE CALCULATION I
i MAXUAL OPERATIONAL REQUIREMENT: REPORTS w
Q.DCM OPERATION REOUIREMENT REPORTS In accordance with ODCM sections 2.7.1 and 3.9.2 inoperable radioactive liquid _and gaseous effluent monitoring instrumentation channels remaining in an inoperable condition'for greater than 30 days shall be reported in the Semiannual Radioactive Effluent Release Report.
During the January 1, 1992 - June 30, 199 reporting period there were no monitors inoperable for greater than 30 days.
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SECTION 9 MAJOR CHANGES TO t l'
RADIOACTIVE WASTE TREATMENT SYSTEMS
h MP.JOR CHANGES TO RADIOACIJVE WASTE TREATMENT SYSTEMS In acccrdance with the CPS ODCM section 7.2, licensee-initiated major changes to the liquid, gaseous or solid racloactive' waste treatment systems shall be reported in the Semiannual Radioactive Effluent Release Report. No major changes to the Waste Treatment Systems were reviewed and approved during this reporting. period, i
i l
61
j SECTION 10 NEW LOCATIONS FOR DOSE l CALCULATION AND/OR ENVIRONMENTAL MONITORING u
I-
i
.y-
-NEW LOCATIO1;B FOR DOSE CALCULATION AND/OR ENVIRONMENTAL _ MONITORING In accordance with CPS ODCM sect.on 7.2, new locations for doue calculations and/or en'ironmental monitoring identified by the Annual Land Use Census shall be reported in the Semiannual Radioactive Effluent Release Report.
-The 1992-Annual Land Use Census began on July 23, 1992, and as of August 29, 199?, had not been completed. Results of the 1992 Annual Land Use Census will be provided in the Semiannual Radioactive Effluent Release Report to be submitted after January 1, 1993.
62
I CPS-0DCM' )
ILLINOIS POWER COMPANY CLINTON POWER STATION UNIT 1
.QFFSITE DOSE CALCULATION MANUAL Docket No. 50-461
.)-
CLINTON-1 Rev.8-7/91
CPS-ODCM .
Illinois Power. Company Clinton Power Station !U N ,, ,,
NSiN ;
03,ia.;h,, uij.U Il!
OFFSITE DOSE CALCULATION MANUAL Jul 31 1991 Table of Contents $$
C0WfliGRED COPY CrlH'*4 f!!\VER STAT l0F Section Title Pace l
1.0 PREFACE 1-1 1.1 Definitions 1-1 1.2 General Operation Requirements 1-4 1.3 General Surveillance Requirements 1-4 2.0 LIQUID EFFLUENTS 2-1 2.1 Introduction 2-1 2.2 Liquid Radwaste Discharge Process Radiation 2-1 Monitoring (PRM) System 2.3 10CFR20' Release. Rate Limits 2-1
).
2.3.1 Liquid Effluent Concentration - 2-2 Operation and Surveillance Requirements 2.3.2 Liquid Radwasta Discharge PRM 2-6 Setpoints 2.3.3 ' Plant Service Water. Effluent 2-11 PRM Setpoints 2.3.4 Shutdown Service Water (SX) 2-12 Effluent PRM Setpoints-2.3.5 Fuel Pool Heat Exchanger Service 2-12 Water Effluent PRM Setpoints 2.4 10CFR50, Appendix I Release Rate Limits 2-13 2.4.1 10CFR50, Appendix I Release Rate 2-13 Limits - Operation and Surveillance Requirements
]
CLINTON-1 i Rev.8-7/91
- m. . - - .
-Illinois Power Company Clinton Power Station 1 OFFSITE-DOSE CALCULATION MANUAL 1
Table of contents Section Title Pace J 2.0 2.4.2 Discussion 2-14 2.5 Liquid Radwaste Treatment System 2-26 2.5.1 Liquid Radwaste Treatment System - 2-26 Operation and Surveillance Requirements 2.5.2 Temporary Liquid Radwasta 2-27 Hold-up Tanks 2.6 Doses From Other Significant Liquid Effluent 2-28 Pathways 2.7 Radioactive Liquid Effluent Monitoring 2-29 Instrumentation 2.7.1 Radioactive Liquid Effluent 2-29 Monitoring Instrumentation -
Operation and Surveillance 3 Requirements 3.0 GASEOUS EFFLUENTS 3-1 3.1 Introduction 3-1 3.2 Gaseous Effluent Release Point Monitoring 3-1 HVAC Stack Process Radiation 3-1 3.2.1 Monitoring (PRM) System 3.2.2 SGTS Stack Process Radiation 3-2 Monitoring (PRM) System 3.3 Main Condenser Off-Gas Monitoring System 3-3 3.3.1 Pre-Treatment Air Ejector Off-Gas 3-3 PRM 3.3.2 Post-Treatment Air Ejector Off-Gas 3-3 PRM 3.4 10CFR20 Release Rate Limits 3-4 l
L CLINTON-1 11 Rev.6-12/89
. - - __ __ _ . _ _ . ..m . _ _
LCPS-ODCM Illinois Power Company Clinton Power Station OFFSITE DOSE CALCULATION MANUAL Table of Contents Section Title Page 3.0 3.4.1 10CFR2O Release Rate Limits - 3-4 Operation and Surveillance Requirements 3.4.2 Dose Rate Due to Noble Gases 3-8 3.4.3 Dose Rate Due to Radiciodines, 3-8 Particulates and Tritium 3.5 10CFR50, Appendix I Release Rate Limits 3-15 3.5.1 Noble Gas Dose - Operation.and 3-15 Surveillance Requirements 3.5.2 Iodine-131, Iodine-133, Tritium, 3-16 and Radionuclides in-Particulate Form - Operation and Surveillance Requirements 3.5.3' Noble Gas Air Dose Equations 3-17 3.5.4 Radiciodines, Particulates and 3-18 Tritium Dose Equations 3.6 Gaseous Radwaste (Offgas) Treatment 3-27 3.6.1 Gaseous Radwaste (Offgas 3-27 Treatment) System - Operation and Surveillance Requirements 3.7 Ventilation Exhaust Treatment 3-28 3.7.1 Ventilation Exhaust Treatment 3-28 System -_ Operation and Surveillance Requirements 3.8 Eftluent Monitor Setpoint Calculations 3-29 3.8.1 Total Body Dose Rate Setpoint 3-29 3.8.2 Skin Dose Rate Setpoint 3-31
)
CLINTON-1 111 Rev.6-12/89
. CPS-ODCM Illinois Power Company Clinton Power Station OFFSITE-DOSE CALCULATION MANUAL Table of Contents Title Pace Section Radioactive Gaseous Monitoring Instrumentation 3-33 3.0 3.9 Offgas Radiation Monitoring 3-33 3.9.1 Instrumentation - Operation and Surveillance Requirements 3-39 3.9.2 Radioactive Gaseous Effluent Monitoring Instrumentation -
Operation and Surveillance -
Requirements 4-1 4.0 COMPLIANCE WITH 40CFR190 Total Dose - Operation and Surveillance 4-1 4.1 Requirements 4-2 9
4.2 4.1.a Special Report Requirements )
5-1 5.0 IIADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 5-2 5.1 Monitoring Program.- Operation and Surveillance Requirements Land Use Census.- Operation and 5-24 5.2 Surveillance Requirements Interlaboratory' Comparison Program 5-26 5.3 Interlaboratory Comparison 5-27 5.3.1 Program - Operation and Surveillance Requirements 6-1 6.0 BASES FOR OPERATION'AND SURVEILLANCE REQUIREMENTS General Operation and Surveillance 6-1 6.1 Requirements Monitoring Instrumentation 6-2 6.2 6-3 6.3 Radioactive Effluents Liquid Effluents 6-3 6.3.1 CLINTON-1 iv Rev.6-12/89
CPS 20DCM Illinois Power Company Clinton Power Station OFFSITE DOSE CALCULATION MANUAL Table of contents Section Title Pace 6.0 6.3.2 Gaseous Effluents 6-5 6.3.3 Total Dose 6-7 6.4 Radiological Environmental Monitoring 6-8 7.0 REPORTING REQUIREMENTS 7-1 t 7.1 . Annual Radiological Environmental Operating 7-1 Report 7.2 Semiannual. Radioactive Effluent Release 7-2 Report 8.O ADIUSTMENT OF THE CPS ODCM METHODOLOGY 8-1
)
t 9.0 ATMOSPHERIC TRi dLPORT AND DISPERSION MODEL 9-1 l
9.1 Introduction 9-1 t- 9.2 Concurrent Meteorological Data Processing 9-1 9.2.1 Determination of Pasquill 9-2 Stability Class 9.2.2* ' Calculation of Stack Height 9-2 Wind Speed 9.2.3 Determination of Release Mode 9-3 and the Entrainment Coefficient l 9.2.4 -Calculation of Vertical Standard 9-4 I Deviation 9.2.5 Calculation of the Building Wake 9-5 Correction 9.2.6 Calculation of Momentum Plume Rise 9- 5 9.2.7 Calculation of Effective Plume 9-6 I Height CLINTON-1 v Rev.6-12/89 ;
s A,. O.d- 6. & - ,- 5 -m n~t-CPS-ODCM-Illinois Power.. Company Clinton Power Station OFFSITE DOS' CALCULATION MANUAL j Table of Contents Title Pace
- Secti&D ,_
Determination of Affected Sectors 9-7 9.0 9.2.8 Calculation of Depletion and 9-7 9.2.9 Deposition Factors 9.2.10 Ground Level X/Q,-D2DPXQ, D1XQ, 9-12 D/Q Analysis 9.2.11' Elevated X/Q, D2DPXQ, D1XQ, D/Q 9-13 Analysis
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n CLINTON-1 vi Rev.6-12/89 i
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, ICPS-ODCML j Z111nois PowerfCompany l Clinton' Power Station- _.
OFFSITE DOSE CALCULATION MA! MAL Tables t
Table Title Pa4e 1.1-l' Surveillance Frequency Notation 1-5 2.3-1 Radioactive biquid Waste Sampling and Analysis ;-3 Program 2.4-1 Adult Ingest!on Dose Commitment Factors - Aij 2-16 2.4-2 . i toaccumulation ' Factors - BFi 2-19
-2.4-3 Adult Ingestion Dose Factors - DFi 2-20
~2.7-1 Radioactive Liquid Effluent Monitoring 2-29 Instrumentation-2.7-2 -Radioactive Liquid Effluent Monitoring 2-31
-Instrumentation surveillance Requirements
).
3.4-1 Radioactive-Gaseous' Waste Sampling and Analysis 3-5
. Program, 9
3.4-2 Dose Factors For Noble Gases and Daughters 3-10 3.4-3 Inhalation Pathway Dose Rate. Factors (Child) - Pii 3-11
-3.4-4 Annual Doses-in Unrestricted Artas 14 '
3.9.1-1 'Offgas Radiation Monitoring Instrumentation 3-34
- i
'3.9.1-2 Offgas Radiation Monitoring Instrumentation 3-37 Surveillance Requirements
'3.9.2-1 . Radioactive: Gaseous Effluent Monito-ing 3-40 Instrumentation 3.9.2-2 Radioactive Gaseous Effluent Monitoring' 3-43 Instrumentation Surveillance Requirements 3.5-1 ; Inhalation Dose--Factors For Infant-(DFA1)a 7-48 13.5 -Inhalation Dose Factors
- Child-(DFAi) a 3-91
.y _
ICLINTON-1 vii Rev. 6-12/89 i
= _ . , , . - _ . _ , - _
CPS-ODCM 1111 nolo Power Cempany Clinton Power Station i OFFSITE DOSE CALCULATION KA!TUAL Tabiqa Title Pace
,Ta)Ll2 3-54 j 3.5-3 Inhalation Dose Factors For Teen-(DFA1)a 3-57 3.5-4 Inhalation Dose Factors For Adult-(DFA1)a 3-60 !
3.5-5 Ground Plane Dose Factors-DFGi 4
Ingestion Dose Factors For Infant-(DFLi)3 3-62 i 3.5-6 ;
Ingestion Dose Factors For Child-(DFLi)a 3-65 3.5-7 Ingestion Dose Factors .For Teen-(DFLi)a 3-68 3.5-8 )
Ingestion Dose Factors For Adult-(DFLi)a 3~71 3.5-9 !
C Input Parameters For Calculating Raij 3-74 3.5-10 M 3-75 3.5-11 Input Parameters For calculating Raij V )l 3-76 3.5-12 Input Parameters For Calculating Raij i I l 3-77 3.5-13 Inhalation Pathway Factors - Raij (INFANT)
I (CHILD) 3-80 3.5-14 Inhalation Pathway Factors - 7 313 I '
l TEEN) 3-83 3.5-15 Inhalation Pathway Factors Rag j I
3-86 3.5-16 Inhalation Pathway Factors - R 13 3 (ADULT)
C 3-89 3.5-17 Cow Milk Pathway Factors - Raij (INFANT)
C 3-92 3.5-18 Cow Milk Pathway Factors - Raij (CHILD)
C 3-95 3.5-19 Cow Milk Pathway Factors - Raij (TEEN)
C J-98 j 3.5-20 Cow Milk Pathway Factors - Raij (ADULT)
C 3-101 3.5-21 Goat Milk Pathway Factors - Raij- (INFANT)
C 3-104 3.5-22 God r. Milk Pathway Factors - Raij (CHILD) i C i Goat Wilk Pathway Fare. ors - Raij (TEEN) 3-107 3.5-23 C
Goat Milk Pathway Factors - Raij (ADULT) 3-110 3.5-24 J
CLINTON-1 viii Rev.5-2/89 l
l
CPS-CDCM Illinois Power Company l Clinton Power Station OFFSITE DOSE CALCULATION MANUAL Tables Table Title Pace M
3.5-25 Moat Pathway Factors - Raij (CHILD) 3-113 M
3.5-26 Meat Pathway Factors - Raij -(TEEN) 3-116 M
3.5-27 Meat Pathway Factors - Raij (J.DULT) 3-139 V
3.5-28 Vegetation Pathway Factors - Ra ij (CHILD) 3-122
. V 3.5-29 Vegetation Pathway Factors - Rali (TEEN) 3-125 V
3.5-30 Vegetation Pathway Factors - Raij (ADULT) 3-128 G
3.5-31 Ground Plane Pathway Factors - Ri 3-129 5.1-1 Radiological Environmental Monitoring Program 5-4 Reporting Levels for Radioactivity Concentrations 5.1-2 5-16 in Environmental Samples 5.1-3 Detection capabilities for Environmental Sample 5-17 Analysis Lower Limit of Detection B
5.1-4 Environmental Report (Operating License Stage) 5-20 2 Table 6.1-8 Requirements . -
9.2-1 Gaseous Effluent Release Point Characteristics 9-15 e
CLINTON-1 ix Rev.6-12/89
1 CPS-0DCM l Illinois Power Cor.pany Clinton Power Station l 1
I OFFSITE DOSE CALCULATION MANUAL E1911LQA
&qurg Title Pace 2.1-1 Unrestricted Area Boundary For Liquid Effluents 2-10 1
Liquid Radwante Treatment System 2-23 l 2.5-1 ;
I 2.5-2 Shutdown and Fuel Pool Heat Exchanger Service 2-24 Water Eftluent Monitors ,
l 2.5-3 Solid Radwaste System Simplified Flow Diagram 2-25 i l
3.1-1 CPS Site Boundary For Gaseous Efflurmts 3-46 ;
3.3-1 ' Main Condenser Off-Gas Treatment System 3-47 l 5.0-1 REMP Locations Within 1 Mile of CPS 5-28 5.0-2 REMP Locations 1-2 Miles From CPS S-29 5.0-3 REMP Locations 2-5 Miles From CPS 5-30 . <
)!
5.0-4 REMP Locations Greater Than 5 Miles From CPS 5-31 l
4
)
l CLINTON-1 x Rev.6-12/C9
CPS-0DCH List of Eff.ective Panes Pace Revision Paco Revision Paco Revision Pace Revision
! i 8 3-2 6 3-54 1 3-106 6 11 6 3-3 6 3-55 5 3-107 5 iii 6 3-4 6 3-56 5 3-108 5 iv 6 3-5 7 3-57 5 3-109 5 y 6 3-6 6 3-58 1 3-110 5 l vi 6 3-7 8 3-59 5 3-111 5 vil 6 3-8 6 3-60 5 3-112 5 viii 5 3-9 6 3-61 5 3-113 5 ix 6 3-10 6 3-62 1 3-114 5 x 6 .3-11 6 3-63 1 3-115 5 x1 8 3-12 , 6 ..
1 3-116 5 xii 8 3-13 :: 6 E. 3-64 3-65 5 3-117 5 1-1 6 3-145 . 6 4 3-66 5 3-118 5 1-2 6 3-15$5 -6 S U 3-67 6 3-119- 5 1-3 6 3-16u G $6 ? 50 3-68 1 3-120 5 l 1-4 8 3-17[d:;
3-18 is( E [66$dM 5 3-69 3-70 5
1 3-121 3-122 5
5 1-5 6 3-1 6 3-39M':j, n6 S S g 3-71 1 3-123 5 2-2 6 6 3 -7 2 5 3-124 6 2-3 6 3-2 3-21H0to l2 ff, '} E,5 @Q- 3-73 1 3-125 5 2-4 6 3-22:; 5 55 3-74 1 3-126 5 52-5 8 3-23$ 6 E$ 3-75 1 3-127 5 2-6 6 3-24 1 3-76 1 3-128 5 2-7 6 3-25 6 3-77 5 3-129 5 2-8 6 3-26 1 3-78 5 3-130 5 2-9 6 3-27 6 3-79 5 3-131 5 3-80 5 4-1 6 l 2-10 8 3-28 6 6 3-81 5 4-2 6 2-11 6 3-29 2-12 6 3-30 6 3-82 5 5-1 6
.2-13 6- 3-31 6 3-83 5 5-2 6 2-14 6 3-32 5 3-84 5 5-3 6 2-15 6 3-33 6 3-85 5 5-4 6 6
2-10 5 3-34 6 3-86 5 5-5 2-17 5 3-35 6 3-87 5 5-6 6 5 5-7 7 3-18 5 3-36 6 3-88
'2-19 5 3-37 6 3-89 5 5-8 6 5 3-38 6 3-90 5 5-9 6 3-20 2-21 5 3-39 6 3-91 5 5-10 6 2-22 5 3-40 8 3-92 5 5-11 6 8 3-41 8 3-93 5 5-12 7
-.2-23 6 2-24 8 3-42 8 3-94 6 5-13 2-25 8 3-43 6 3-95 5 5-14 6 2-26 6 3-44 6- 3-96 5 5-15 6 2-27 8 3-45 6 3-97 5 5-16 6 6 3-46 8 3-98 5 5-17 6 3-28 2-29 6 3-47 8 3-99 5 5-18 6 2-30 6 3-48 5 3-100 5 5-19 6 3-31 7 3-49 5 3-101 5 5-20 7 2-32 6 3 5 3-102 .5 5-21 7 3-103 5 5-22 7
'3-33 6 3-51 5 6
2-34 6 3-52 1 3-104 5 5-23 3-53 1 3-105 5 5-24 6 3-1 2 CLINTON x! Rev.8-7/91
. - . . ~ - - -- .,-
_ _ _ = _ _ . _ . - _. . _
. = _ - . . - - . - - . . . - - _ _
t CPS-ODCM List of Effective Pacos 1-Pace Revisign 5-25 6 5 6 5-27 6-5-28 7 ,
5-29 6 5-30 7 l 5
l ' 5-31 8 6-1 6 6-2 6 6-3 6 6-4 6 6-5 .6 6-6 6 6 '6 6-8 6 6-9 6 7-1 6 l 7-2 8 7-3 6 7-4 6 8-1 6 9-1 '6 )
9-2 6 9-3 6 9 -7 9-5 6 9-6 6 9-7 6 9-8 6 9-9 6 9-10 6-9-11 6 ,
9-12 6 9-13 6 9-14 6 9-15 6
]
CLINTON-1 xii Kev.8-7/91
CPS-ODCM 1.0 GENERATION IN70RMATIOff PREFACE i
The Clinton Power ~ Station OFFSITE DOSE CALCULATION MANUAL (CPS-ODCM) provides the methodologies and paramotors to be used by Illinois Power Company (IPC) to assure compliance with the radioactive effluent dose limitations staced in 10CFR20, 10CFR50 Appendix A (GDC60 and 64), 10CFR50 Appendix I, and 40CFR190.
The CPS-ODCM was prepared based on guidance provided in NUREG-0133, PREPARATION OF RADIOLOGICAL EFFLUENT TECHNICAL SPECIFICATIONS FOR NUCLEAR POWER PLANTS (October 1978), and NUREG-0473, RADIOLOGICAL EFFLUENT TECHNICAL SPECIFICATIONS FOR BOILING WATER REACTORS (Draft 7, to Rovision 3). This manual along with station proceduren will be used by CPS personnel to demonstrate compliance with the above referenced Federal Regulations.
Changes to the CPS-ODCM shall be provided in tho SEMIANNUAL RADIOACTIVE RELEASE REPORT.
1.1 Definitions The following terms are defined so that uniform interpretation of requirements of this manual may be achieved. The defined terms appear in capitalized type and shall be applicable throughout this manual.
)
CHANNEL CALIBRATION 1.1.1 A CHANNEL CALIBRATION shall be the adjustment, as nocessary, of the channel output such that it responds with the necessary range and accuracy to known valuca of-the parameter which the channel monitors. The CHANNEL CALIBRATION shall encompass the entire channel including the sensor and alarm and/or trip functions, and shall include the CHANNEL FUNCTIONAL TEST. The CHANNEL CALIBRATION may be performed by any series of sequential, overlapping or total channel steps such that the entire channel is calibrated.
CHANNEL CHECE 1.1.2 A CHANNEL CHECK shall be the qualitative assessment of channel behavior during operation by observation. This determination shall include, whero possible, comparison of the channel indication and/or status with other indications and/or status derived from independent instrument channels measuring the same paramotor.
I CLINTON-1 1-1 Rev.6-12/89
,_ . , - _ _ - . - _ _ _ . ~ . - . , _ _ - . - - - . - _ _ _.
CPS-ODCM CHANNEL FUNCTIONAL TEST 1.1.3 A CHANNEL FUNCTIONAL TEST shall be:
- a. Analog channels - the injection of a simulated signal into the channel as close to the sensor as practicable to verify OPERABILITY, including alarm and/or trip functions and channel failure trips.
- b. Distable channels - the injection of a simulated signal into the sensor to verify OPERABILITY including alarm and/or trip functions.
The CHANNEL FUNCTIONAL TEST may be performed by any series of sequential, overlapping or total channel steps such that the entire channel is tested.
FREOUENCY NOTATION 1.1.4 The. FREQUENCY NOTATION specified for the perforrance of surveillr.nce requirements shall correspond to the intervals defined in Tablo 1.1-1.
GASJOUS RADWASTE TREATMENT SYSTEM 1.1.5 A GASEOUS RADWASTE TREATMENT SYSTEM is any system designed and installed to reduce radioactive gaseous effluents by collecting primary coolant system offgases from the main condenser evacuation 3 system and providing for delay or holdup for the purpose of reducing the total radioactivity prior to release to the environment.
MEMBERIS) OF THE PUBLIC ,
1.1.6 MEMBER (S) OF THE PUBLIC shall include all persons who are not occupationally associated with the plant. This cctegory does notAlso include employees of the licensee, its-contractors or vendors.
excluded from this category are persons who enter the site to service equipment or to make deliveries. This category does include persons who use portions of the site for recreational, occupational or other purposes not associated with the plant.
l OPERABLE - OPERABILITY 1.1.7 A system, subsystem, tra!.n, component or device shall be
' OPERABLE or have OPERABILITY when it is capable of performing its l l specified function (s) and when all necessary attendant i
instrumentation, controls, electrical power, cooling or seal water, lubrication or other auxiliary equipment that are required for the j system, subsystem, train, component or device to perform its ;
function (s) are also capable of performing their related support l I
function (s).
f l
CLINTON-1 1-2 Rev.6-12/89
\
CPS-ODCM REMEDIAL REOUIREMENT 1.1.8 REMEDIAL REQUIREMENT shall be that part of a requirement which prescribes remedial measures required under designated conditions.
SITE BOUNDARY 1.1.9 The SITE BOUNDARY shall be that line beyond which the land is neither owned, nor leased, nor otherwise controlled by the licensee.
SOURCE CHECK 1.1.10 A SOURCE CHECK shall be the qualitative assessment of channel response when the channel sensor is exposed to a source of increased radioactivity.
UNRESTRICTED _ AREA 1.1.11 An UNRESTRICTED AREA shall be any area at or beyond the SITE BOUNDARY access to which is not controlled by the licensee for purposes of protection of individuals from exposure to radiation and radioactive materials or any area within the SITE DOUNDARY used for residential quarters or for industrial, commercial, institutional, and/or recreational purposes (see Figure 2.1-1).
VENTILATION EXHAUST TREATMENT SYSTEM 1.1.12 -A VENTILATION EXHAUST TREATMENT SYSTEM is any system designed and installed to reduce gaseous radiolodine or radioactive material in particulate form in effluents by passing ventilation or vent exhaust gases through charcoal adsorbers and/or HEPA filters for the purpose of removing iodines or particulates from the gaseous exhaust stream prior to the release to the environment. Such a system is not considered to have uny effect on noble gas effluents.
Engineered Safety Feature (ESP) atmospheric cleanup syntoms are not considered to be VENTILATION EXHAUST TREATMENT SYSTEM components.
The following systems are designated VENTILATION EXHAUST TREATMENT SYSTEMS
- 1) Machine Shop HVAC (VJ)
-2) Laboratory HVAC (VL)
- 3) Drywell Purge (VQ)
- 4) Radwaste Bldg HVAC (VW)
/
CLINTON-1 1-3 Rev.6-12/89
_ _ _ . . ... _ . . _ _ _ _ _ _ _ _ _ _ _ . _ _ _ _ . . . _ . _ . _ _ . _ _ _ _ _ _ _ . ~ _ _ . _ . _ . _ _ _
CPS-ODCH 1.2 General oneystion Requirements 1.2.1 Compliance with the Operation Requirement contained in the succeeding requiremente is required during the conditions specified therein;-except that upon failure to meet the Operation Requirement, the associated REMEDIAL REQUIREMENT shall be met.
1.2.2 Hnncompliance with a requirement shall exist when the requirements of the Operation Requirement are not met and the associated REMEDIAL REQUIREMENT (s) is not met within specified time limits or intervals.
1.3 General Surveillsnee Recuirements 1.3.1 Surveillance Requirements shall be not during the applicable .
conditions specified in and for the associated operation Requirement unless stated in the individual Surveillance Requirement.
1.3.2 .Each Surveillance Requirement shall be performed within the specified time interval with a maximum allowable extension not to exceed 25 percent of the specified surveillance interval.
1.3.3 Failure to perform a Surveillance Requirement within the specified time interval shall constitute a failure to meet the OPERABILITY requirements for a Operation Requirement. . Surveillance requirements do not have to be performed on inoperable equipment.
1.3.4 Entry into a specified system operating mode shall not be )
made unless the Surveillance Requirement (s) associated with the Operation Requirement have been performed within the applicable surveillance interval or as otherwise specified.
[
CLINTON-1 1-4 Rev.8-7/91 l
E - . _._
. _ . . . _ _- . _ . . ~ . . . _._ _ . _ - _ - . . _ - . _ _ _ . _ . _ . _ . _ . . _ _ . . _ _
> CPS-ODCM i i
TABLE 1.1-1 SURVEILLANCE FREOUENCY_liOTATION 1
NOTATION FREOUENCY S At least once por 11 hours1.273148e-4 days <br />0.00306 hours <br />1.818783e-5 weeks <br />4.1855e-6 months <br />.
D . At least onco per 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> W At least once per 7 days. .
M At least once per 31 days.
Q At least once per 92 days. ,
SA At least once per 184 days.
A At least once por 366 days ,
R At least onco per_18 months (350 hap).
P: Prior to each release.
S/U Prior to each reactor startrq.,
liA liot applicable.
~
1
?! . .
- CLINTON 5 Rev.6-12/89 wr.w w v ua,4, g .mic'e .gs g,ey.q g i, ww* pem.-9.n. ye p .,y,y y pc#gw3.p,g&,w,,ayw.g >n p.%9 ppwwq.w. .w ;see9. g.%% wy3e , yq,p -ey .m.nen, ,, 4,Mwe.aye s q.T , .-. _
9
CPS-ODCM 2.0 LIOUID EFFLUE!1TS 2.1 Introduction 3 Liquid radwasto offluent coloased from CPS will moot 10CFR20 concentration limits at the point of dischargo to the unrestricted area shown in Figure 2.1-1, This design and operation objectivo will be achieved at all times. Actual dischargos of liquid radwasto offluent will occur on a batch basis and the average concentration
- at the point of dischargo will normally be only a small percentage of the allowed limits. Refer to Clinton USAR Section 11.5 for a description of radiation monitoring, sampling and offluent control systems.
Cumulativo quarterly deso contributions due to radioactivo effluents released to the unrestricted area will bo datormined once overy 31 !
days using NUREG-0133 and Regulatory Guido 1.109 methodology and paramotors.
2.2 Licuid Radwaste Discharno Process Radiation Monitorina (PRM) Synten This monitoring subsystem measures liquid radwaste offluent radioactivity prior to the offluent joining plant service water and circulating water dilution st cams. A high radioactivity signal from this gamma scintillation detector automatically terminatos the liquid radwanto offluent release. The liquid radwaste offluent c) flow, variablo from 10-60 GPM or 50-300 GPM, combinos with Plant Servico Water flow (minimum flow approximately 5000 GPM during plant ).
shutdovn periods depending on system loads) and Plant Circulating Water flow (0-567,000 GPM) in the Seal Well prior to entoring the 3.4-milo discharge flume to Lake Clinton (soo Figure 2.5-1) .
2.3 10CFR20 Release Rate Limits The operation and Surveillanco Requirements portaining to dischargo of liquid raduasto effluent to the unrestricted area are specified in Section 2.3.1 as follows.
4 CLINTON-1 2-1 Rev.6-12/89 e ., - ~,-..-w.,.w--..w-., . , --.-...r.m..,,._n. . . . , , c,y.,.,y-., -. w,-- 7 , , , , -y . - , . ,,,.%..~,,y , , . . . . , - , -
, , , . , . _ n y.-,m-w=m---,
CPS-0DCM 2.3.1 Liquid Effluent Concentration - Operation and Surveillance Requirements OPERATION PEOUTREMENT The concentration of radioactive material released in liquid effluent to UNRESTRICTED AREAS (see Figure 2.1-1) shall be limited to the concentrations specified in 10 CFR Part 20, Appendix B, Table II, Column 2 for radionuclides other than dissolved or entrained nobio gases. For dissolved or entrained noble gases, the
, concentration shall be limited to 2 x 10~ microcuries/ml tetal activity. This requirement applies during all releases via this l pathway.
REMEDIAL PEOUIREMENT l With the concentration of radioactive material released in liquid offluents to UNRESTRICTED AREAS exceeding the above limits, I immediately restore the concentration to within the above limits.
l pyRVETLLANCE REOUTREMENTS 2.3.1.1 -Radioactive liquid wastes shall be sampled and analy od according to the 'ampling s and analysis program of Ttble 2.3-1.
) 2.3.1.2 The results of the radioactivity analyses shall be used in accordance with the methodology and parameters of Section 2.3.2 to I assure that the concentrations at the point of release are i maintained within the limits of the above operation Requirement.
l f
l l
i I
i CLINTON ,
Rev.6-12/89
-- ,s , _ . - y e ..-s m<,_,._.,,-7 ..y ..,---.e - - - , ~ - , , ,%ve,,.,--- -.,,v,,-,.- w..-,rw-,,.,--,----.--,.+,,-=mw-m -
. _ _ . ~ . _ . _ . .._ _,._ _. _ _._,_ _,,_,,_,_ , _ , , _ _ _ _ _,
-l l
CPS-ODCM l I
TABLE 7.3 1 1 RADIOACTIVE LIOUID WASTE SAMPLING AND ndALYSIS PROGRAM I
LOVER LIMIT MINIMUM OF DETECTION LIQUID RELEASE SAMPLING ANALYSIS TYPE OF ACTIVITY (LLD)" :
TYPE FREOUFNCY FRFOUENCY ANALYSIS (1 Ci /ml) j A. Batch Waste P P i
Each Batch Each Batch Principal Gamina 5x10*7 )
Releage Emitters" Tanks .
1 131 1x10 6 i
P M Dissolved and 1x10-5 One .n/M Entrained Cases j
(Gannna Emitters)
P Q H3 1x10 5 d
Each Batch Composite Gross Alpha 17.10*7 ,
i P Q- Sr 89, Sr 90 5x10*8 d
Each Batch Composite Fe-55 1x10 6 CLINTON-1 2-3 Rev.6-12/89
. _ . . . , _ _ _ , . _ _ , .. -. _. _ .____.____ ~, _..._.__, . . _ _ _ . . _ . _
CPS-ODCM i
TABLE 2.3-1 (Continued)
RADIOACTIVE LIOUJD WASTE SAMPLING AND ANALYSIS PROGRIsM TABLE NOTATIONS aThe LLD is defined, for purposes of these requirements, as the smallest concentration of radioactive material in a sample that will yield a net count, above systen 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: -
4.66 sb LLD =
E x V x 2. 22 x 10 6 x Y x exp (-lat)
Where:
LLD is the "a priori" lower limit of detection as defined above, as microcuries per unit mass or volume, sb is the standard deviation of the background counting rate or of the counting rate of a blank sample as appropriate, as counts per minute.
E is the counting efficiency, as counts per disintegration, V is the sample size in units of mass or volume, 2.22 x 10 6 is the number of disintegrations per minute per .
microcurie, Y is the fractional radiochemical yield, when applicable, A is (sec_ghe
) andradioactive decay conctant for the particular radionuclide at for plant offluents is the elapsed time between the midpoint of sample collection and the time of counting (sec).
Typical values of E, V, Y and at should 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 nosteriori (after the fact) limit for a particalar measurement.
l CLINTON-1 2-4 Rev.6-12/89 l
CPS-ODCM i TABLE 2.3-1 (Continuedi l RADIOACTIVE LIOUID WASTE SAMPLING AND ANALYSIS PROGRAM TABLE NOTATIONS (Continued)-
, bA batch release is the discharge of liquid wastes of a discrete volume, ,
Prior to sampling for analyses, the tank is isolated from all inputs and !
recirculated a minimum of two tank volumes at which time a sample is obtained for isotopic analysis. I C The principal gamma emitters for which the LLD requirement applies !
include the following radionuclides Mn-54, Fe-59, Co-58, Co-60, 2n-65, l
Mo-99,_Cs-134, Cs-137, a Co-144 shall also be measured, but with an LLD of 5 x 10~6.nd Ce-141.This list does not mean that only these i nuclides are to be detected and reported. Other gamma peaks that are measurable, together with those of the above nuclides, shall also be analyzed and reported in the Semiannual Radioactive Effluent Release Report pursuant to Technical Specification 6.9.1.7 in a format outlined in:Regulatcry Guide 1.21, Appendix B, Revi.mion 1, June 1974. I dA composite sample is one in which the quantity of liquid sampled is proportional to the quantity of liquid waste discharged and in which the method of sampling employed results in a specimen that is representative of the liquids released. , ,
)f l
t I
2-5 Rev.8-7/91 CLINTON-1
CPS-ODCM To comply with the above requirements, setpoints will be calculated to assure that Seal Well concentrations do not exceed 10CFR20, Appendix B, Table II, Column 2 values at any time.
2.3.2 Liquid Radwante Discharce PRM Setooints To corply with the Operation Requirements of Section 2.3.1 and Section 2.7.1, the alarm / trip netpoints for liquid effluent monitors and flow measurement devices are set to assurn that the following equation is satiLfied:
cf 1 CMPC (1)
F+f CMPC = the effluent concentration limit (Section 2.3.1) implementing 10CFR20 for the site, corresponding to the specific mix of radionuclides in the effluent stream being considered, in pCi/ml c = the setpoint, in pCi/ml, of the radioactivity monitor measuring the radioactivity concentration in the effluent 3
line prior to dilution and subsequent release; the setpoint is inversely proportional to the volumetric flow of the effluent line and proportional to the volumetric flow of the dilution stream (s)
- plus the offluent stream.
F = the dilution water flow setpoint as determined at the Seal Well,.in volume per unit time f = The liquid radwaste discharge flow setpoint as determined at the liquid radwaste discharge PRM location, in volume per unit time (same units as F)
The available dilution water flow (F) should be constant for a given release, and the liquid radwaste tank discharge flow (f) and monitor setpoint (c) are set to meet the condition of equation (1) for a given affluent concentration (CMPC). The method by which this is accomplished is illustrated in sections 2.3.2.1 chrough 2.3.2.5.
CLINTON-1 2-6 Rev.6-12/89
CPS-ODCM 2.3.2.1 The isotopic concentration for a liquid radwaste tank to be discharged is obtained from the sum of the measured concentrations as determined by the analyses required in Table 2.3-1:
riCi = EgCg+IaCa+ES Cs+C T +Cro, pCi/ml (2) wh9re EC gg = The sum of concentrations Cg of each measured gamma emitter g (including I-131) observed by gamma spectroscopy of the waste sample, ci/ml.
IaCa = The sum of-concentrations Ca of alpha emitters (a) in liquid radwaste as measured in the most current QUARTERLY composite discharge tank sample, pCi/ml.
Escs = The sum of concentrations Cs of Sr-89/Sr-90 in liquid radwaste as observed in.the most current QUARTERLY
' composite discharge tank sample, pCi/ml.
CT = The measured concentration of H-3 in liquid radwaste as determined from analysis of the most current QUARTERLY composite discharge tank sample, pC1/ml.
Cye = The measured concentration of Fe-55 in liquid radwaste as observed in the most current QUARTERLY !
composite discharge tank sample, gCi/ml.
2.3.2.2 The measured radionuclide concentrations are used to 1 calculate a DILUTION FACTOR (DF) which is equivalent to the ratio of total dilution flow rate to liquid radwaste tank effluent flow rate required to. assure that the limiting concentrations of 10CFR20, Appendix B, Table II, Column 2 are met at the point of discharge to the unrestricted area.
DF = SF [ Ici ), dimensionless (3)
MPC l =
SF [ ICg + Ica + ICs + CT +CeF ]
8 MPCpe 9MPC g aMPCa MPCs MPCT
.where
= The measured concentrations Cg, C a' C s, C, Ici 7 i C,p as defined in equation (2), pC1/m] .-
CLINTON-1 2-7 Rev.6-12/89
.. + - . . , , . . . , . . . .n, , , . , .
. ... .. -. _~ - - - _~ . - _ _ . _ - . _ - - . . _ _ - _ - - -
4 CPS-ODCH MPCi = The limiting concentration of the corresponding radionuclide MPC MPC , HPC T, MPC from 10CFR20, Appendik,B, T$ble IS,, MPCColumn 2,FepC1/ml. ',
For dissolved or entrainod noble gases, the concentration shall be limited to 2E-04 uCi/ml total activity.
SF = The conservative SAFETY FACTOR normally applied to compensate for statistical fluctuations and measurement errors, dimensionless.
2.3.2.3 The maximum permissible liquid radwaste tank effluent flow rate, Ftank, is calculated by the following equation:
Ftank = 0.9 (Fdil + ftank), volume / time (4)
DF where Fdil = Minimum expected dilution water flow rate (Circulating and/or Service Water systems),
volume / time ftank = Maximum expected liquid radwaste tank effluent flow rate, volume / time 1
0.9 = Flow rate correction factor to provide a 10% margin '
for variations in flow rates, dimensionless DF = The DILUTION FACTOR calculated by equation (3),
dimensionless Equation (4)~is valid only for DF21; for DF<1, the liquid radwaste tank effluent concentration meets the limits of 10CTR20 without dilution and therefore Ptank may assume any value not to exceed discharge pump capacity. .
2.3.2.4 The liquid radwaste discharge PRM setpoint may now be specified based on the values of E C4 i (Eq.2) and F tank (Eq.4) which were determined to provide compliance with the concentration limits of 10CFR20, Appendix B, Table II, Column 2. The monitor response is primarily a gamma response and the actual setpoint is therefore based on EC (Eq.2). The monitor setpoint, in counts per m$nEte (cpm), which corresponds to the particular setpoint concentration, Cg, is determined based on monitor calibration data or operational data which correlates monitor response to sample analyses associated with the actual liquid radwaste discharged.
The second method is considered valid only if the integrity of laboratory methods of determination are 1 proven more accurate than the monitor data.
CLINTON-1 2-8 Rev.6-12/89
l CPS-ODCM l
The set point concentration, Cg, is obtained by the )
following equation Egg C , pCi/ml (5)
Cg = (Ftank) f act ;
where f act a The actual liquid radwaste i effluent flow rate, volumo/ time ]
If (Ftank/ fact)hl, the value obtained for Cg is used to l determine the monitor setpoint above background, l cepm, from either of the two methods described above. ;
1 In the case where (Ftank/ fact)<1, no release may be ;
made using the existing discharge parameter values (DF, Ftank, fact I * )
The setpoint concentration is conservative, even if F tank is attainable, since the calculated flow rate contains the SAFETY FACTOR, dilution flow rate and
' liquid raovaste tank effluent flow rate margins, I
2.3.2.5 To prevent spurious alarms, revise the Plant Service )
)
Water Effluent PRM s-tpoint to coincide with the secpoint concentration, Cg, calculated by equation (5). ,
This setpoint is valid only during periods of actual liquid radwaste discharges.
l 1
CLINTON-1 2-9 Rev.6-12/89
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CPS-ODCM 2.3.3 Plant Service Water Effluent PRM Setooints Plant service watur effluent continuously releases to the Seal Well where it mixes with circulating water effluent (if present) prior to entering Lake Clinton via thu 3.4 mile discharge flume.
The plant service water effluent is not considered a radioactive discharge pathway unless liquid radwacte discharges are in progress or any service water cooling load heat exchanger has been detected as failed. To ensure that Plant Service Water intersystem leakage has not occurred, weekly Service Water !
effluent grab samples will be obtained (when in service) and analyzed to determine the identity and quantity of principal gamma-omitting radionuclides. In addition, a quarterly composite of positive grab samplas will be analyzed to determine the quantity of H-3, Sr-89, Sr-90, Fe-55 and gross alpha species released. The analytical Lower Limit of Detection (LLD) for these analyses are specified in Table 2.3-1.
If the weekly grab sample analysis indicates the absence of contamination above background, the Plant Service Water effluent PRM setpoint-should be established as close to background as practical to prevent upurious alarms, and yet assure an alarm should an inadvertent release cecur, If the weekly grab sample analysis indicates the presence of contamination above background, PRM setpoints will be established following section 2.3.2 methodology as followst 2.3.3.1 Perform section 2.3.2.2, sciving equation (3) for DF using the appropriate values in the concentration term from the grab sample analysis.
2.3.3.2 A modified dilution factor, DFm, must be determined so that available dilution flows may be apportioned among simultaneous discharge pathways. The modified dilution factor is defined as:
DFm = DE (6)
F3 where F3 is an administrative allocation factor which may be assigned any value between 0 and 1 under the condition that I (Fg )n 8 1 (7) n and where n = the number of liquid discharge pathways for whica DF al and which are planned for simultaneous release. For simplicity, F3 may be assigned the value '
1/n. Calculate F in equation (4) by substituting the value of DF for hnkand perform the calculation specified in section $.3.2.4 to determine Ilow rate and PRM setpoints.
CLINTON-1 2-11 Rev.6-12/89
CPS-ODCM 2.3.4 Shutdown Service Water (SX) Effluent PRM Setpoints Shutdown Service Water, when initiated, is a potential continuous radioactive discharge pathway to the Ultimato Heat Sink (UHS) (see Figure 2.5-2). The SX effluent is not conuidored a radioactivo discharge pathway unless any SX cooling load heat exchanger has been detected as failed. SX effluent sampling, analysis and sotpoint establishment will be performed as discussed for the Plant Service Water system in Section 2.3.3.
2.3 5 Fuel Pool Heat Exchanger Service Water Effluent PRM Sotpoints The Fuel Pool Heat Exchanger Servico Water is noimally supplied by the Component Cooling Water (CCW) system (a closed loop system). The CCW system rejects heat loads to the Plant Service Water system where intersystem leakago would be detected as described in section 2.3.3. The Fuel Pool Heat Exchanger Service Water effluent is considered a potential radioactivo discharge pathway when SX replacos CCW as the heat sink for the fuel pool heat exchangers. To account for a potential batch release of CCW radioactivity to the Ultimato Heat Sink.via SX, CCW will be sampled and analyzed as discussed in section 2.3.3.
The analysis results will then be used to establish Fuel Pool Heat Exchanger Service Wator PRM and flow rate sotpoints following Section 2.3.3.1 and 2.3.3.2 methodology.
) Any releases of radioactivity to the environment from the Plant Service Water (except during liquid radwaste discharges),
Shutdown Service Water or - Fuel Pool Heat Exchanger Servico Water Systems are considered abnormal events. Such events will be accounted for as unplanned releases in the SEMIANNUAL RADIOACTIVE EFFLUENT RELEASE REPORT.
s CLINTON-1 2-12 Rev.6-12/89
CPS-ODCM 2.4 10CFA50. Annendix I Releaso Rate Linits The Operation and Surveillance Requirements concerning 10CFR50, Appendix I Release Limits are specified in section 2.4.1 as follows.
C;-e calculations for ensuring compliance with these limits are d..eussed in section 2.4.2.
2.4.1 10CTR50, Appendix I Release Rate Limits - Operation and Surveillance Rsquirements ,
OPERATION PECUTREMENT The dose or dose commitment to a MEMBER OF THE PUBLIC from radioactive materials in liquid affluents released to UNRESTRICTED AREAS (see Figure 2.1-1)-shall be limited:
- o. During any calendar quarter to less than or equal to 1.5 mrems to the total body and to less than or equal to 5 mrems to any organ, and b,_ During any calendar year to less than or equal to 3 mrems to the total body and-to less than or equal to 10 mrems to any organ.
This requirement applies at all times.
REMEDIAL REOUTREMENT:
- 0. - With the calculated dose from the release of radioactive materials in liquid effluents exceeding any of the above limits, prepara and subm3 ;
to the Regional Administrator of the Regional Office offor the exceeding NRC withi.
30 days a Special Report that identifies the cause(s) the limit (s) and to reduce-the defines the corrective actions that have been taken releases and the proposed corrective actions to be taken to assure that subsequent releases will be in compliance with the above limits.
SURVEILLANCE REOUTREMENTS 2.4.1.1 Cumulative dose contributions from liquid effluents for the current calendar quarter and the current calendar year shall be determined in accordance with the methodology and parameters described in Section 2.4.2 at least once per 31 days.
CLINTON-1 2-13 Rev.6-12/89
CPS-0DCM 2.4.2 Discussion 2.4.2.1 The dose contribution to the maximum exposed individual from all radionuclides identified in liquid effluents released to the unrestricted area is calculated as follows:
m Dj = ri Ai$y ,El ati C 11F 1, mrom (8) where Dj , = The cumulative calendar quarter or yearly dose to any organ j from liquid effluent for the total release period, mrem t1 = The length of the 1th release time period over which C11 and F1 are averaged for liquid releases, hours
= Liquid Radwaste Tank Volume / Liquid Radwaste Discharge Flow Rate C11 = The average concentration of nuclide i in undiluted liquid effluent during release period ati for any liquid release, Ci/ml F1 = The near field average dilution factor for C11 dur4ng any liquid effluent release, dimensionless. Defined att the ratio of the average undiluted liquid radwaste flow during the release, to the product of the average flow from the discharge structure (during the reporting period, i.e., quarter or year) to the unrestricted receiving water and Z
= Averace Undiluted Licuid Waste Flow (9)
(Average Discharge Structure Flow)Z Z = The applicable dilution factor for Lake clinton, dimensionless
= 1.0 Aji = The composite ingestion dose commitment factor for the total body or critical organ of an ADULT for
.radionuclide 1, mrem /hr per uci/ml
=KoUy + U gBFi DF i. (10)
Uw CLINTON-1 2-14 Rev.6-12/89 x
- - . . -. .- - . ~ . . - . - . . . - . - . - - _- - -- . - -..
CPS-ODCM-where Ko = A units conversion factor, 1 14E405 pCi-ml-yr/pci-liter-hr !
= (1. 0E+06 eCi/uci) 8760 hr/yr (1.0E+03 ml/ liter)
Uy = ' Annual water consumption by the maximum adult, 0 liter /yr Dy = Dilution factor from the near field area to the nearest potable water intake, 1.0 Ug = Adult fish consumption rate, 21 kg/yr (Table E-5 of Regulatory Guide 1.109)
= Bioaccumulation factor for radionuclide i in fish, BFi pCi/kg per pCi/ liter (Table 2.4-2 taken from Table A-1 of Regulatory Guide 1.109)
= Adult ingestion dose conversion factor for, radionuclide DFi i, total body or critical organ, mrem /pci:(Table 2.4-3 taken from Table E-11 of Regulatory Guide'1.109)
Table 2.4-1 contains values for Ai$ as calculated by equation (10).
The quarterly limits specified in the OPERATION REQUIREMENT at )
- j the beginning of this section represent ene-half of the annual '
design objective of Section II.A of 10CFR50, Appendix I.
1 i
l l
l l
2-15 Rev.6-12/89 CLINTON-1
- - .,. , . - , ., . , . . _ , . - - . - - , - , , , , . , n_.,- -.- , ,
_,m -___m. . - _ _ _ -- . . _ _ _ . _ . -
- CPS-ODCM i
l TAT.LE 2.4-1 ADULT INOESTION DOSE COMMITMENT FACTORS Ai j (arem/hr per pCi/ml)
ISOTOPE BONE LIVE'R T. BODY THYROID KIDNEY LUNG GI L1,L.,,,,,
H3 NO DATA 2.26E.01 2.26E.01 2.26E 01 2.26E.01 2.26E.01 2.26E 01 -
C-14 3.12E+04* 6.24E+03 6. 2I,1+03 6.24E+03 6.24E+03 6.24E+03 6.24E+03 NA.24 4.06E+02 4.06E+02 4.06E+02 4.06E+02 4.06E+02 4.06E+02 4.06E+02 P 32 1.39E+06 a.o2E404 . 5.36E+04 NO DATA NO DATA NO DATA 1.$6E+05 CR 51 - NO DATA NO DATA 1.27E+00 7.60E 01 2.80E 01 1.68E+00 3.20E+02 MN 54 NO DATA 4.37E+03 8.34E+02 NO DATA 1.30E+03 NO DATA 1.34E+04 MN 56 NO DATA 1.10E+02- 1.95E+01 NO DATA 1.40E+02 NO DATA 3.51E+03 FE.55 6.57E402 4.54E+02 1.06E+02 NO DATA NO DATA 2.53E+02 2.60E+02 FE 59 1.04E+03 - 2.44E+03 9.34E+02 NO DATA NO DATA- 6.81E+02 8.13E+03 CO.58 No DATA 8.90E+01 - 2.00E+02 NO-DATA NO DATA NO DATA 1.80E+03 CO.60 NO DATA 2.56E+02 5.64E+02 NO DATA NO DATA NO DATA 4.80E+03 NI 63 3.11E+04 2.15E+03 1.04E+03 NO DATA NO DATA NO DATA 4.49E+02 NT.65 1.26E+02- 1.64E+01 7.48E+00 NO DATA NO DATA NO DATA 4.16E+02 CU.64 NO DATA 9.97E+00 4.67E+00 NO DATA 2.51E+01 NO DATA 8.48E+02 ZN 65 -2.31E+04 7. 36E444 3.33E+04 NO DATA 4.92E+04 NO DATA 4. 64 E &O4 EN,69 4;92E+01 9.42E+01- 6.55E+00 NO DATA 6.12E+01 NO DATA 1 *1E+01 BR 83 NO DATA- NO DATA 4.03E+01 NO DATA NO DATA NO DATA 5.81E+01 BR.84 NO DATA - NO DATA - 5.23E+01 NO DATA NO DATA NO DATA 4.10E 04 BR 85 NO DATA NO DATA 2.15E+00 NO DATA' NO DATA NO DATA LT E 15**-
RB.86- NO DATA 1.01E+05 4.70E+04 NO DATA NO DATA NO DATA 1.99E+04 R0 88 - NO DATA 2.89E+02 1.53E+02 NO DATA NO DATA NO DATA 4.00E 09 RB.89 NO DATA 1.92E+02 1.35E+02 NO DATA NO DATA NO DATA 1.11E.11 SR 89. 2.21E+04 NO DATA 6.34E+02 NO DATA NO DATA NO DATA 3.54E+03 SR-90 5.43E+05 NO DATA 1.33E+05 NO DATA NO DATA NO DATA 1.57E+04 SR 91 4.06E+02 NO DATA 1.64E+01 NO DATA NO DATA NO DATA 1.94E+03 SR-92 1.54E+02 Nu DATA 6.67E+00 NO DATA- NO DATA NO DATA 3.05E+03 Y.9^ 5.75E.01 NO DATA 1.54E 02 No DATA NO DATA NO DATA 6.10E+03
- CLINTON-1 2-16 Rev.5-2/89
- ru.g-.., ,-y,. . , _ 4- .+.y, ... , , , , , - . _ ,_,,w,Sg.,, ,.m .,, ,.m ,_,.--.,--_,mg_y, .,,e ,,7y,mm e , v. ,%- .4my -y,, , , . , -
. . _ _ _ . _ _ . _ _ _ . _ . _ . . _ . _ _ _ _ _ . . _ _ _ _ . _ . ~ . _ _ . _ _ _ . _ _ _
J CPS-0DCM i
i l
TABLE 2.4-1 feontinued)
)
ADULT INGESTION DOSE COMMITMENT TACTORS Ai j I
(mrem /hr per #Ci/mi)
T. BODY THYROID KIDNEY LUNG CI tLI TSOTOPE QF LIVER 2.10E 04 NO DATA NO DATA NO DATA 1.60E 02 Y 91m 5.43E 03 NO DATA 4.64E+03 2.25E 01 NO DATA NO DATA NO DATA Y 91 8.42F400 NO DATA 1.48E 03 NO DATA NO DATA NO DATA 8.84E+02 Y 92 5.03E 02 NO DATA NO DATA NO DATA 5.0BE+03 j Y 93 1.60E 01 NO DATA 4.42E 03 NO DATA 5.20E 02 NO DATA 1.21E 01 NO DATA ? 44E+02 ;
ZR 95 2.40E 01 7.69E 02 2.67E 03 1.22E 03 NO DATA 4.04E-03 NO DATA 6.28E+02 ZR 97 1.32E 02 l
2.48E+02 1.33E+02 NO DATA 2.45E+02 NO DATA 1.51E+06 i NB 95 4.46E+02 1.03E+02 1.96E+01 NO DATA 2.33E+02 NO DATA 2.39E+02 MO 99 NO DATA TC 99m 8.86E 03 2.50E 02 3.19E 01 NO DATA 3.80E-01 1.23E 02 1.48E+01 I
TC 101 9.11E 03 1.31E 02 1.29E-01 NO DATA 2.36E 01 6.70E 03 3.94E 14 ,
NO DATA 1.90E+00 NO DATA 1.69E+01 NO DATA 5.16E+02 RU 103 4.42E+00 2.25E+02 RU 105 3.68E 01 NO DATA 1.45E 01 NO DATA 4.7/1 c00 NO DATA 8.32E+00 NO DATA 1.2.r+02 NO DATA 4.25E+03 )
RU 106 6.57E+01 NO D.
NO DATA NO DA1A NO DATA NO DATA NO DATA NO DATA AG 110m NO DATA 1.02E+04 9.28E+02 3.43E+02 7.70E+02 1.04E+04 NO DATA TE 125m 2.57E+03 7.89E+02 1.65E+03 2.63E+04 NO DATA 2.17E+04 TE 127m 6.47E+03 2.31E+03 3.77E+01 2.28E+01 7.79E+01 4.28E+02 NO DATA 8.300 03 TE-127 1.05E+02 5. 54 E+ 04 4.10E+03 1.74E+03 3,78E+03 4.59E+04 NO DATA TE 129m 1.10E+04 7.31E+00 2.30E+01 1.26E+02 NO DATA 2.26E+01 TE 129 3.00E+01 1.13E+^1 6.74E+02 1.28E+03 8.19E+03 NO DATA 8.03E+04 TE 131m 1.65E+03. 8.09E4 2 NO DATA 2.67E+00
.TE 131 ^1.88E+01 7.87E+00 5.95E+00 1.55E+01 8.25E+01 1.50E+04 NO DATA 7,37E+04 TE 132 2.41E+03 1.56E+03 1.46E+03 1.72E+03 6.78E+03 1.25E+02 NO DATA 6 . 8 t' E+01 1 130 2.71E+01 7.99E+01 3.15E+01 1,22E+02 6.99E+04 3.66E+02 NO DATA -5 o35+01 1-131 1.49E+02 2.13E+02 6.81E+00 6.81E+02 3.10E+01 NO DATA 3.66E+00 1 132' 7.28E+00 1.95E+01 2.70E+01 1,30E+04 1.54E+02 NO DA1A 7.96E+01
'I-133 5.09E+01~ 8.85E+01 No DATA 9.00E 03 1 134 3.80E+00 1.03E+01 3.69E+00 1.79E+02 1.64E+01 CLINTON-1 2-17 Rev.5-2/89
CPS-ODCM TABLE 2.4 m (cont inuecQ ADULT INCESTION DOSE COMMITHENT FACTORS Ai j (arem/hr per 401/ml)
UOTOPE BONE LIVER T. BODY THYROID KIDNEY LUNG CI.LLI 1 135 1.59E+01 4.16E+01 1.53E+01 2.74E+03 6.67E+01 NO DATA 4.70E+01 CS 134 2.97E+05 7.07E+05 5.78E+05 NO DATA 2.29E+05 7.60E+04 1.24E+04 CS.136 3.11E+04 1.23E+05 8.84E+04 NO DATA 6.84E+04 9.37E+03 1.40E+04 CS 137 3.81E+05 5.21E+05 3.41E+05 NO DATA 1.77E+05 5. 88E+04 - 1. 01E+04 CS.138 2.64E+02 5.21E+0e 2.58E+02 NO DATA 3.83E+02 3.78E+01 2.22E 03 BA 139 9.29E.01 6.60E-04 2.72E.02 NO DATA 6.18E 04 3.75E 04 1.65E+00 BA.140 1.94E+02 2.44E 01 1.27E+01 NO DATA 8.29E 02 1.40E 01 4.00E+02 BA 141 4.50E 01 3.40E 04 1.52E 02 NO DATA 3.16E.04 1.93E 04 2.12E 10 BA.142 2.04E.01 2.09E.04 1.28E.02 NO DATA '
77E 04 1.18E.04 2.89E 19 4
LA 140 1.49E-01 7.53E.02 1.99E 02 NO DATA NO DATA NO DATA 5.53E+03 1A.142 7.65E.03 3.48E.03 8.66E.04 NO DATA NO DATA NO DATA 2.54EA01 CE 141 2.24E.02 1.51E.02 1.72E.03 NO DATA 7.03E 03 NO DATA 5.78E$01
)
CE.143 3.94E 03 2.92E+00 3.23E.04 NO DATA 1.28E.03 NO DATA 1.09E+02 CE.144 1.17E+00 4.88E.01. 6.26E 02 NO DATA- 2.89E.01 NO DATA 3.94E+02 PR 143 5,50E.01 2.20E.01. 2.72E 02 NO DATA 1.27E 01 NO DATA 2.41E+03 PR.144 1.80E 03 7.47E 04' 9.14E.05 NO DATA 4.21E 04 NO DATA 2.59E 10-ND.14r 3.76E 01 4.34E 01 2.60E.02 NO DATA 2.54E 01 NO DATA 2.08E+03
.W 18) 2.95E+02' 2.47E+02- 8.63E+01 NO DATA NO DATA NO DATA' P.09E+04 NP 239 2.84E-02 2.80E.03 1.54E.03 NO DATA 8.72E-03 NO DATA 5.74E+02 -
- - 3.12 x 104
- Less than 10*15 CLINTON-1 2-18 Rev.5-2/89
CPS-ODCM ,
TABLE 2.4-2 BI0 ACCUMULATION FACTORS -BFi (pci/kg per pCi/ liter)
FRESF 3TER ELEMENT _ .FI . ___
H 9.0E-01 C 4.6E+03 Na 1.0E+02 P 3.0E+03 Cr 2.0Ev02 Mn 4.0E+02 Fe 1.0E+02
- Co 5.0E+01 Ni 1.0E+02 Cu 5.0E+01 Zn 2.0E+03 Br 4.2E+02 Rb 2.0E+03 Sr 3.0E+01 Y 2.SE+01 Zr 3.3E+00 Nb 3.0E+04 Mo 1.0E+01- )
Tc 1.5E+01 Ru 1.0E+01-Rh 1.0E+01 Te 4.0E+02 I- 1.5E+01 Cs- 2.0E+03 Ba 4.0E+00 La- 2.5E+01 Ce 1.0E+00 Pi '
2.5E+01 94 2.5E+01 J , , ,, _, ,
1.2E+03 1.0E+01 CGINCON-1 2 1,', Rev.5-2/89
CPS-ODCM TABLE 2.4-3 ADULT INGESTION DOSE FACTORS DFt (mrem /pCi ingested)
N!!CLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI H3 NO DATA 1.05E-07 1.05E-07 1.05E 07 1.05E 07 1.05E 07 1.05E-07 C-14 2.84E-06* 5.68E-07 5,68E-07 5.68E-07 5.68E-07 5.68E-07 5.68E-07 F.*-24 1.70E 06 1.70E 06 1.70E 06 1.70E-06 1.70E-06 1.70E 06 1.70E 06 P 32 1.93E-04 1.20"-05 7.46E-06 NO DATA NO DATA NO DATA 2.17E.05 ~
CR-51 NO DATA NO DATA 2.66E-09 1.59E-09 5.86E-10 3.53E 09 6.69E 07 KN 54 NO DATA 4.57E-06 8.72E 07 NO DATA 1.36E-06 NO DATA 1.40E 05 MN 56 NO DATA 1.15E-07 2.04E-08 NO DATA 1.46E-07 NO DATA 3.67E 06 FE 55 2.75E-06 1.90E-06 4.43E-07 NO DATA NO DATA 1.06E 06 1.09E 06 FE 59 4.34E 06 1.02E-05 3.91E-06 NO DATA NO DATA 2.85E-06 3.40E-05 CO 58 NO DATA 7.45E 07 1.67E 06 NO DATA NO DATA NO DATA 1.51E-05 CO-60 NO DATA 2.14E-06 4.72E-06 NO DATA NO DATA NC DATA 4.02E-05 1.30E-04 9.01E-06 4.36E 06 NO DATA NO DATA . NO DATA 1.88E-06
) NI 63 l
o NI 65 5.28E 07 6.86E-08 3.13E-08 NO DATA NO DATA NO DATA 1.74E-06 b,[f CU.64 NO DATA 8.33E-08 3.91E-08 NO DATA 2.10E 07 NO DATA 7.10E-06
'y ZN-65 4.84E 06 1.54E-05 6.96E-06 NO DATA 1.03E 05 NO DATA 9.70E-06 f _-
IN-69 1.03E-08 1.97E-08 1.37E-09 NO DATA 1.28E-08 NO DATA 2.96E-09 -
BR 83 NO DATA NO DATA 4.02E 08 NO DATA NO DATA NO DATA 5.79E-08 BR-84 NO DATA NO DATA 5.21E-08 NO DATA NO DATA NO DATA 4.09E-13 BR-85 NO DATA NO DATA 2.14E 09 NO DATA NO DATA NO DATA LT E-24**
RB 86 NO DATA 2.11E-05 9.83E-06 NO DATA NO DATA NO DATA 4.16E 06 RB-88 NO DATA 6.05E 08 3.21E-08 NO DATA NO DATA NO DATA 8.36E-19 RB 89 NO DATA 4.01E 08 2.82E-08 NO DATA NO DATA NO DATA 2.335;-21
- b 8) 3.08E-04 JO DATA 8.84E-06 NO DATA NO DATA NO DATA 4.94E-05 56-90 7.58E-03 NO DATA 1.86E-03 NO DATA NO DATA NO DATA 2.19E-04 SR-91 5.67E-06 UO DATA 2.29E-07 NO DATA NO DATA NO DATA 2.70E-05 SR-92 2.15E-06 NO DATA 9.30E-08 NO DATA NO DATA NO DATA 4.26E 05 Y-90 9.62E-09 NO DATA 2.58E-10 NO DATA NO DATA NO DATA 1.02E-04 i
CLINTON-1 2-20 Rev.5-2/89 1
CPS-ODC2{
. TABLE 2.4-3 (continued)
ADULT INGESTION DOSE FACTORS - DFt (mrem /pci ingested)
LIVER T. BODY THYROID KIDNEY LUNG -
GI-LLI NUCLIDE BONE 3.52E 12 NO DATA NO DATA NO DATA 2.67E.10
-T 91m 9.09E 11 NO DATA 3.77E 09 NO DATA NO DATA NO DATA 7.76E 05
-Y 91 1.41E 07 NO DATA NO DATA 1.4SE 05 2.47E 11 NO DATA NO DATA Y 92 8.45E 10 NO DATA 7.40E 11 NO DATA. NO DATA NO DATA 8.50E 05 Y 93 2.68E 09 NO DATA NO DATA 3.09E-05 ZR-95 3.04E 08 9.75E 09 6.60E 09 NO DATA 1.53E-08
'1.55E-10 NO DATA 5.12E-10 NO DATA 1.05E 04 ZR-97 1.68E 09 3.39E-10 1.86E 09 NO DATA 3.42E 09 NO DATA 2.10E-05 NB 95 6.22E-09 3.46E-09 9.99E-06 NO DATA 4.31E 06 8.20E 07 NO DATA 9.76E 06 NO DATA MO 99 3.42E-10 4.13E-07 2.47E-10 6.98E-10 8.89E 09 NO DATA 1.06E-08
-TC 99m 3.59E 09 NO DATA 6.59E-09 1.87E-10 1.10E 21 TG 101 2.54E 10 3.66E-10 2.16E-05 1.85E-07 NO DATA 7.97E-08 NO DATA 7.06E-07 NO DATA RU-103 NO DATA 9.42E-06 1.54E 08. NO DATA 6.08E 09 NO DATA 1.99E-07 RU 105 5.31E-06 NO DATA 1.78E 04 )
RU 106 2.75E-06 NO DATA 3.48E 07 NO DATA 6.04E-05 8.79E-08 NO DATA 2.91E-07 NO DATA AC-110m 1.60E-07 1.48E-07 1.07Es05
-3.59E 07 8.06E-07 1.09E-05 NO DATA TE-125m 2.68E 06- 9.71E-07 1.73E 06 2.75E 05 NO DATA 2.27E-05 TE-127m 6.77E-06 2.42E-06 8.25E-07 8.15E-08 4.48E 07 NO DATA S.68E 06 TE-127- 1.10E 07 :3.95E ?S 2.38E-08 5,79E-05 1.15E-05 4.29E-06 1.82E-06 3.95E 06 4.80E 05 NO DATA TE-129m 7.65E 09 2.41E 08 1.32E-07 NO DATA 2.37E 08
-TE 129 3.14E 08 1.18E-08 8.40E 05 7.0$E 07 1.34E 06 8.57E-06 NO DATA' TE-131m -1.73E 06 8.46E-07 2.79E 09
'1.97E 08 .8.23E-09 6.22E-09 1.62E 08 8.63E-08 NO DATA
-TE-131-1.80E-06 1.57E-05 NO DATA 7.71E 05 TE 132 2.52E 06. 1.63E-06 1.51E-06 1.89E-04 3.48E-06 NO DATA 1.92E-06
-I 130 7.56E 07 2.23E-06' 8.80E 07 1.95E 03 1.02E-05 NO DATA 1.57E-06
% 131 4'.16E-06 5.95E-06 3.41E 06 1.90E 05 8.65E-07 NO DATA 1.02E-07 I-132 2.03E-07 '5.43E-07 1.90E 3.63E 04 4.31E 06 NO DATA 2.22E-06 I-133 1.42E-06 2.47E-06 7.53E-07 4.99E-06 4.58E-07 NO DATA 2.51E-10
-I-134- 1.06E-07 2.88E 07 1.03E-07 2-21 Rev.5-2/89 CLINTON-1
CPS-0008 i
L TABLE 2.4-3 (continued)
ADULT INGESTION DOSE FACTORS DFi (arem/pci ingested)
NUCLTDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI I-135 4.43E-07 1.16E 06 4.28E-07 7.65E-05 1.86E 06 NO DATA 1.31E 06 CS-134 6.22E 05 1.48E 04 1.21E 04 NO DATA 4.79E 05 1.59E 05 2,59E 06 CS-136 6.51E 06 2.57E 05 1.85E-05 NO DATA 1.43E 05 1.96E 06 2.92E-06 CS-137 7.97E 05 1.09E 04 7.14E 05 NO DATA 3.70E 05 1.23E-05 2.11E 06 CS-138 5.52E-08 1.09E-07 5.40E 08 NO DATA 8.01E-08 7.91E-09 4.65E 13
-BA-139 9.70E 0E' 6.91E-11 2.84E 09 NO DATA 6.46E-11 3.92E 11 1.72E 07 BA 140 2.03E-05 2.55E-08 1.33E 06 NO DATA 8.67E-09 1.46E 08 4.18E 05 BA 141 4.71E-08 3.562 11 1.59E-09 NO DATA 3.31E 11 2.02E 11 2.22E !17 BA-142 2.13E 08 2.19E-11 1.34E 09 NO DATA 1.85E 11 1.24E 11 3,00E 26 LA-140 2.50E 09 1.26E 09 3.33E 10 NO DATA NO DATA NO DATA 9.25E 05 LA-14T 1.28E 10 5.82E-11 1.45E 11 NO DATA NO DATA NO DATA 4.25E 07 CE-141 9.36E 09 6.33E 09 7.18E-10 NO DATA 2.94E-09 NO DATA 2.42E 05
)
-CE 143 1.65E 09 1.22E-06 1.35E-10 NO DATA 5.37E-10 NO DATA 4.56E 05 CE-144 4.88E 07 2.04E-07 2.62E-08 NO DATA 1.21E 07 NO DATA 1.65E-04 PR-143 9.20E-09 3.69E 09 4.56E-10 NO DATA 2.13E-09 NO DATA 4.03E 05 PR-144 3.01E-11 1.25E 11 1.53E 12 NO DATA 7.05E-12 NO DATA 4.33E 18 ND-147 6.29E-09 7.27E 09 4.35E-10 NO DATA 4.25E-09 NO DATA 3.49E-05 V-187 1.03E-07 8.61E-08 3.01E-08 NO DATA NO DATA NO DATA 2.32E 05
-NP-239 1.19E-09 1.17E-10 6.45E-11 NO DATA 3.65E-10 NO DATA 2.40E 05
~* 2.84 X 10-06
- Less than 10-24 CLINTON-1 2-22 Rev.5-2/89
- CPS-ODCM FIGURE 2.5-1 LIQUID RADWASTE TREATMENT SYSTEM A
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- Monitors required by Section 2.7 OWZO1P Chem. Ust. 2WF04T Floor Drain OWE 02PA,b, and C Waste
-lWF0lS Floor Drain Evsporator Evap. Tank Pump Evaporator Tank Samp. Tk Pumps
' 2WF0lS Floor Drain OVE01FA,B, and C OWZ0lT Chem. Waste OWE 0lTA and B Excess Evaporator Waste Filters Evaporator Tank Water Tanks 0VZOlS Chemical OVE01DA,B, and C IVF04P Fir. Drn. 0WE0lPA and B Excess Wasta Evaporator Waste Demins Evap. Tank Pump Water Tank Pumps
- lWF04T. Floor Drain OVE02TA,B, and C 2WF04P Fir. Drn. 1PR036 Service
' Evaporator Tank Waste Sample Tks. Evap. link Pump Water PRM OPR040 Liquid RW Discharge PRM CLINTON-1 2-23 Rev.8-7/91
CPS-ODCM FIGURE 2.5-2 SHUTDOWN AND FUEL POOL HEAT EXCHANGER SERVICE WATER EFFLUENT MONITORS 5 C FUCL POOL HEAT WATC# (XCHANGER SERVICE RHR HEAT WAl(R PRW EXCHANC(R "A"
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LOADS SERVICE WATER gymagg CQCUNG HCAI SHUTGWN EFFLUENT "3" .ggag ,
CICHAWR "B" SERVIC' WAfgR 1RIX-PR039* $2NK 1I LOOP "B" ir I j
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". NORMAL COOLING StJPPLY '- COMPONENT COOLING. WATER EMERGENCY COOLING SUPPLY - SHUTDOWN SERVICE WATER
- Monitors required by Section 2.7 i
1RIX-PR038 Shutdown Service 1RIX PR005 Fuel Pool Heat Water Effluent "A" Exchanger Service Water PRM 1RIX-PR039 Shutdown Service -lRIX-FR004 Fuel Pool Heat Water Effluent "B" Exchanger Service Water PRM i
CLINTON-1 2-24 Rev.8-7/91
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l CPS-ODCM 2.5- Licuid Radwaste Treatment System 2.5.1 Liquid Radwaste Treatment System - Operation and Surveillance Requirements OPERATION REOUTREMENT The liquid radwaste treatment system shall be OPERADLE. The appropriate portions of the system (Figure 2.5-1) shall be used to reduce the radioactive materials in liquid wastes prior to their discharge when the projected doses _due to the liquid effluent to UNkESTRICTED AREAS (see Figure 2.1-1) would exceed 0.06 mrem to the total body or 0.2 mrem to any organ in a 31-day period. This requirement applies at all times.
REMEDIAL REOUIREMENT:
- a. With radioactive liquid waste being discharged without trettment and in excess of the above limits and any portion of the liquid radwaste treatment system not in operation prepare and submit to the Regional Administrator of the Regional Office of the NRC within 30 days a Special Report that includes the following information:
1
- 1. Explanation of why liquid radwaste was being discharged without' treatment, 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. 4 SURVEILLANCE REOUIREMENTS 2.5.1.1 Doses due to liquid releases to UNRESTRICTED AREAS shall be projected at least once por 31 days in accordance with the methodology and. parameters described in Section 2.4.2.
'2.5.1.2 The liquid-radwaste treatment'shall be demonstrated OPERABLE by meeting the Operation Requirements of Section 2.3.1 and 2.4.1.
CLINTON-1 2-26 Rev.6-12/89
, 2.5.2- Temporary Licuid Radwaste Hold-un Tanks The use of temporary liquid radwaste hold-up tanks may occur at CPS. To Lcomply with_ Technical Specification 3.7.7, the curie-limit for liquid redwaste stored in such_ tanks may be calculated using the methodology presented in Appendix B of NUREG-0133 (BWR-RATAFR code), but limited to loss than or equal to 10 curies, excluding tritium and dissolved or entrained noble gases.
1
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l CLINTON-1 2-27 Rev.8-7/91
CPS-ODCM 2.6 Doses From Other Sionificant Licuid Effluent Pathways Sect' ion 2.4 of this manual is based upon the aquatic food and potable
-water exposure pathways only. Other exposure pathways, namely shoreline deposits and irrigated foods, may arise at Clinton Power Station and will be included in.the-section 2.4 dose contribution if they are likely to provide a significant contribution to-the total dose. A pathway is considered significant if a conservative evaluation yields an additional dose increment equal to or more than 10 percent of the total from all other existing pathways. Methods for calculating doses from other poteatially significant liquid effluent pathways are presented in Appendix A to Regulatory Guido 1.109.
When it is determined that other liquid effluent pathways do exist, the Regulatory Guide 1.109 Appendix A equations and parameters will be used in lieu of site-specific data to determine a pathway's significance.
CLINTON-1 2-28 Rev.6-12/89
CPS-ODCM 2.7 Radioactive Licuid Effluent Monitorina Instrumentation 2.7.1 Radioactive Liquid Effluent Monitoring Instrumentation Operation and Surveillance Requirements OPERATION REQUIREMENT Thr. radioactive liquid effluent monitoring instrumentation channels shown in .J10 2.7-1 shall be OPERABLE with their alarm / trip setpoints set to The alarm / trip ensure _that the limits of Section 2.3.1 are not exceeded.
setpoints of'these channels shall be determined and adjusted in accordance with the methodology and parameters described in Sections 2.3.2 through 2.3.5. This requirement applies during releases via the associated pathway.
REMEQIAL REOUIREMENT:
- a. With a radioactive 11guld effluent monitoring instrumentation channel alarm / trip setpoint less conservative than required by the above requirement, without delay suspend the release of radioactive liquid effluents monitored by the affected channel, or declare the channel inoperable, or change the setpoint so it is acceptably conservative,
- b. With less than the minimum number of radioactive liquid effluent monitoring instrumentation channelo OPERABLI, comply with the Restore the inoperable REMEDIAL REQUIREMENT shown in Table 2.7-1.
instru%ents to OPERABLE status within 30 days and, if unsuccessful, )
expir.in in the next Semiannual Radioactive Effluent Release Report why the inoperability was not corrected in a timely manner.
SURVEILLANCE REOUIREMENTS ,_
2.7.1.1 Each radioactive liquid effluent monitoring instrumentation control shall be demonstrated OPERABLE by performance of the CHANNEL CHECK, SOURCE CHECK, CHANNEL CALIBRATION rnd CHANNEL FUNCTIONAL TEST at the frequencies shown in Table.2.7-2.
CLINTON-1 2-29 Rev.6-12/89
CPS-ODCM --
, TABLE 2.7-1 EADIOACTIVE LIoUID EFFLUENT MONITORING INSTRUMENTATION MINIMUM CHANNELS REMEDIAL OPERABLE REOUIREMENT
- 1. RADIOACTIVITY MONITORS PROVIDING ALARM AND AUTOMATIC TERMINATION OF RELEASE
- a. Liquid'Radwaste Discharge' Process Radiation Monitor 1(a) y
- 2. RADIOACTIVITY MONITORS PROVIDING ALARM BUT NOT PROVIDING AUTOMATIC TERMINATION OF RELEASE
- a. Plant Service Water Effluent Process Radiation Monitor 1(a) 2
- b. Shutdown Service Water Effluent Process Radiation Monitor 1/ Division *I") 2
- c. Fuel Pool Heat' Exchanger Service Water Radiation Monitor 1(a) 2
- 3. FLOW RATE MEASUREMENT DEVICES
- a. Liquid Radwaste Effluent Line 1 3
- b. Plant Service Water Effluent Line 1 3
- 4. TANK LEVEL INDICATING DEVICES
- a. Cycled Condensate Storage 1 4
- b. Reactor Core Isolation Cooling Storage 1 4
" Division I and Division II only.
CLINTON-1 2~30 Rev.6-12/89
- ~ _ _ _
CPS-ODCM TABLE 2,7-1 (Continued),
RADIOACTIVE LIOUID EFFLUENT MONITORING INSTRUMENTATION TABLE NOTATION (a) Channel OPERABILITY shall include the capability of either the Main Control Room Central Control Terminal (MCR-CCT) or the Radiation Protection Office Contral Control Terminal (RP-CCT) to provide the alarm status of the applicable radiation monitor channel (s).
REMEDIAL REOUTREMENT REMEDIAL With the number'of channels OPERABLE less than required by REQUIREMENT the Minimum Channels OPERABLE requirement, effluent i releases may continue via this pathway provided that prior to initiating a release:
- a. At least two independent samples are analysed in accordance with Section 2.3.1.1, and
- b. At least two technically qualified members of the Facility Staff independently verify the release rate calculations and discharge line valving:
Otherwise, suspend release of radioactive effluents via this pathway.
I' REMEDIAL a. With both the MCR-CCT and RP-CCT inoperable perform a REQUIREMENT CHANNEL CHECK using local monitor indication within 8
)
2 hours and at least once per 8 hours9.259259e-5 days <br />0.00222 hours <br />1.322751e-5 weeks <br />3.044e-6 months <br /> thereafter,
- b. With the monitor otherwise inoperabl.i, effluent releases via this pathway may continue provided that at least once per 12 hours1.388889e-4 days <br />0.00333 hours <br />1.984127e-5 weeks <br />4.566e-6 months <br />, grab samples are oactivity at a limit collected and analyzed for r9 dipCi/ml.
of detection of at least 10~
REMEDIAL With'the number of channels OPERABLE less than required-by REQUIREMENT the Minimum Channels OPERABLE requirement, effluent 3 releases via this pathway may continue provided the flow rate is estimated at least once per 4 hours4.62963e-5 days <br />0.00111 hours <br />6.613757e-6 weeks <br />1.522e-6 months <br /> during actual releases. Pump-performance curves generated in place may be used to estimate flow (All flows diverted from Plant L
Service Water must be taken into account when estimating flow).
REMEDIAL With the number of channels OPERABLE less than required by REQUIREMENT the Minimum _ Channels OPERABLE requirement, liquid 4 additions to this tank may continue provided the tank liquid level is estimated during all liquid additions to the tank.
CLINTON-1 2-31 Rev.7-2/91
C PS-O Ds.. -
TABLE 2.7-2 RADIOACTIVE LTOUID EFFLUENT MONITCRING INSTRUMENTATION SURVEILLANCE REOUIREMENTS CHANNEL CIIANNEL SOURCE CIIANNEL FUNCTIONAL CALIBRATION TEST l INSTRUMENT CHECK QIECK
- 1. RADIOACTIVITY MONITORS PROVIDING ALARM AND' AUTOMATIC TERMINATION OF RELEASE
- a. Liquid Radwaste Discharge Process Radiation Monitor .
p p(3) ggy)
Effluent Line D(5)
- 2. RADIOACTIVITY MONITORS PROVIDING ALARM BUT NOT PROVIDING AUTOMATIC TERMINATION OF RELEASE
- a. Plant Service Water Effluent R(3) Q(2)
Process Radiation Monitor D(5) M
- b. Shutdown Service Water Effluent Process Radiation R(3) Q(2)
Monitor D(5) M l
- c. Fuel Pool IIcat Exchanger Service Water Radiation R(3) Q(2)
Monitor D(5) M
- 3. FLOW RATE MEASUREMENT DEVICES
- a. Liquid Radwaste Effluent Line D I4) IIA R Q
- b. Plant Service Water Effluent Line D I4) NA R Q CLINTON-1 2-32 Rev.6-12/89
'f CPS-ODCM.
' TABLE 2.7-2'(Continued)
RADIOACTIVE LTOUID EFFLUENT MONITORING' INSTRUMENTATION SURVEILLANCE REOUIREMENTS-i '. CHANNEL CHANNEL SOURCE CHANNEL- FUNCTIONAL ~
CHECK CHECK CALIBRATION " TEST INSTRUMENI' 4 ~. TANK LEVEL INDICATING DEVICES NA R N A :-
- a. Cycled' Condensate Storage D*
! b. Reactor Core Isolation NA R NA Cooling D*
- During liquid additions 1to the tank.
-i i
4 CLI'~1N-1 ' 33
- Rev.6-12/89:
+
_ CPS-ODCM TABLE 2.7-2 (Cont inu ed_l,
)
RADIOACTIVE LIOUID EFFLUENT MONITORING INSTRUMENTATION SURVEILLANCE REOUIREMENTS TABLE NOTATION",
(1) The CHANNEL FUNCTIONAL TEST shall also demonstrate that automatic isolation of this pathway occurs and that the MCR-CCT or RP-CCT
. provides annunciation and event printout in response to'each of the following conditions:
- 1. Instrument indicates measured levels above the alarm / trip (HIGH) satpoint.
- 2. Detector failure (LOW FAIL, HI FAIL) .
- 3. Sample flow failure (EXTERNAL FAIL) .
- 4. Instrument not set in normal operate mode (UNINITIALIZED, CALIBRATE, MAINTENANCE, or STANDBY.)*
(2) The CHANNEL FUNCTIONAL TEST shall also demonstrate that the MCR-CCT or RP-CCT responds with annunciation and event printout to each of the following conditions:
- 1. Instrumee.t. indicates measured levels above the alarm (HIGH) setpoint.
- 2. Detector failure (LOW FAIL, HI FAIL) .
- 3. Sample flow failure (EXTERNAL FAIL) .
- 4. Instrument not set in ncrmal operate mcde (UNINITIALIZED, C2. LIBRATE , MAINTENANCE, or STANDBY).
(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 haye been obtained from suppliers that participate in measurement assurance activities with NIST. 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 consist of verifying indication of flow during periods of release. CHANNEL CHECK shall be made.at least once per 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> on days which continuous, periodic, or batch releases are made.
(5) The CHANNEL CHECK shall also determine that channel communication is established to the MCR-CCT or RP-CCT.
A. demonstration of automatic isolation of.the release pathway.is.not, applicable to this condition. _
CLINTOF-1 2-34 Rev.6-12/89
CPS-ODCM 3.O. GASEOUS EFFLUENTS -
3.1 Introduction Gaseous effluents from CPS are released on both a batch and continuous
-basis. Gaseous effluents are normally discharged on a long term basis.
High volume Continuous containment Durge and mechanical vacuum pump discharge may be considered short term releases.
There are-two gaseous _ effluent release points to the environment: the Commen Station HVAC Stack and the Standby Gas Treatment System (SGTS)
Stack. The height of these stacks is such that all gaseous effluents are treated as mixed-mode releases (reference Table 9.2-1). The SGTS is an Engineerud Safety Feature filter system utilized following an accident to reduce iodine and particulate activity in gases leaking from the primary containment and which are potentially present in the secondary containment. The Common Station HVAC Stack ("HVAC Stack") receives process and ventilation exhaust from the following inputs:
- 1) Continuous Containment Purge (CCP) l 2) Containment Building Ventilation
- 3) Tarbine Building Ventilation
- 4) Radwaste Building Ventilation
- 5) Auxiliary. Building Ventilation G) Puel Building ventilation
- 7) Auxiliary Building Refrigerant Purge
- 8) Laboratory Ventilation System
- 9) Counting / Equipment Decon Rooms Ventilation )
- 10) Steam Packing Exhauster i 11) Mechanical Vacuum Pump I
- 12) Drywell Purge The effluent exiting the SGTS stack is monitored at the SGTS stack and the combined inputs to the HVAC stack are monitored at the HVAC stack.
All inputs to the 'IVAC Stack, with the exception of input numbers 7 through 10, can be monitored prior to entering the stack.
Figure 3.1-1 delineateu-the CPS site boundary for implementation of gaseous effluent 10CFR20 and 10CFR50, Appendix I Release Rate Limits.
3.2 Gaseous Effluent Release Point Monitorinc 3.2.1 HVAC Stack-Process Radiation Monitorinc (PRM) System The HVAC Stack inputs are monitored for radioactivity pricr to discharge to the environment by the HVAC Stack PRM. The PRM detector configuration provides effluent monitoring using seven (7) channels as follows:
- 1) Beta' scintillator for particulates l
l
.)
CLINTON-1 3-1 Rev.2-10/86 l
. CPS-ODCM ,
2)- Alpha surface barrier detector to account for the radon / thoron contribution to the beta particulate measurement 3} Gamma scintillator for iodine
- 4) Iodine background subtracti'on
- 5) Beta scintillator for low range noble gas
- 6) Energy-compensated Geiger-Mueller (G-M) detector for high range noble gas
- 7) Energy-compensated G-M detector for gamma area subtraction This monitor has no control function but annunciates in the Main Control Room and the Radiation Protection Office where proper response actions will be initiated in accordance with CPS procedures.
3.2.2 EGTS Stack Process Radiation Monitorina (PRM) System As discussed in section 3.1, the SGTS is used to reduce post-accident concentrations of radioactivity in the primary and secondary containment via filter trains. The SGTS Stack PRM s monitors the gaseous effluent of the filter trains at the SGTS
' Stack prior to release to the environment. The PRM detector configuration utilizes nine (9) channels as follows:
- 1) Deta scintillator for particulates
- 2) Gamma scintillator for iodine
- 3) . Iodine background subtraction
- 4) Beta scintillator for low range noble gas
- 5) Energy-compensated G-M detector for intermediate range noble gas
- 6) Energy-compensated G-M detector for gamma area subtraction
- 7) Alpha surface barrier detactor to account for the radon / thoron contribution to the beta particulate measurement CLINTON-1 3-2 Rev.6-12/89
CPS-ODCM l
- 9) Sample flow-rate through the SGTS P_.M 7 This monitor has no control function but annunciates in the Main Control Room and the Radiation Protection Office where proper response actions will be initi-ted in accordance with CPS procedures.
i 3.3 Main Condenser Off-Qas Monitorina System i l
3.3.1 Pre-Treatment Air Eiector Off-Gas Process Radiation Monitor 1 (PRM) l The Pre-Treatment Off-Gas PRM monitors hydrogen recombiner l
)
effluent for gross noble gas radioactivity. This effluent is then routed to the charcoal adsorbers for eventual release to '
the environment via the station HVAC Stack (see Figure 3.3-1) .
The PRM detector configuration consists of a single energy- l compensated G-M detector mounted in a gas volume.
The monitor has no control function but annunciates in the Main Control Room and the Radiation Protection Office where proper response actions will be initiated in accordance with CPS procedures.
3.3.2 Post-Treatment Air Eiector Off-Gas Process Radiation Monitor (PRM).
The Post-Treatment Off-Gas PRM moLitors the gaseous radioactivity at upstream, intermediute or downstream sections of the charcoal adsorber beds prior to the effluent entering the station HVACTheStack PPfor releaseconfiguration detector to the environment (see is as described Figure 3.3-1).
for the HVAC Stack PRM (Section 3.2.1) with the exception of two additional channels which measure sample pressure.
at the PRM and sample flow-rate through the monitor.
The monitor has two control functions. Upon detection the of noble gas activity in excess of the ALERT setpoint, charcoal'adsorber bypass valves shut (if in the charcoal bypass mode) and the off-gas is routed through the adsorbers.
Should noble gas activity exceed the HIGH setpoint, or upon PRM; failure, the off-gas system is automatically isolated from the HVAC Stack and a reactor scram may occur if loss of
-condenser vacuum occurs.
The Main Condenser Off-Gas Treatment System-it shown in Figure 3.3-1.
3-3 Rev.6-12/89 CLINTON-1
l CPS-ODCM 3.4 10CFR20 Release Rate Limits The Operation and Surveillance Requirements concerning 10CFR20 Release Rate Limits are specified in Section 3.4.1 as follows. Dose Rate calculations for ensuring compliance with these limits are discussed in Sections 3.4.2 and 3.4.3.
3.4.1 10CFR20 Release Rate Limits - Operation and Surveillance Requirements OPERATION REOUIREMENT The dose rato due to radioactive materials released in gaseous effluents from the site to areas at and beyond the SITE BOUNDARY (see Figure 3.1-1; shall be limited to the following:
i
- a. .For noble gaces: Less than or equal to 500 mrem /yr to the total
-body and less than or equal to 3000 mrem /yr to the skin, and I For iodine-131, for iodine-133, for tritium, and for all b.
radionuclides in particulate form with half lives greater than 8 days: Less than or equal to 1500 mrem /yr to any organ.
This requirement applies at all times.
} REMEDIAL REOUIREMENT:
With the dose rate (s) exceeding the above limits, immediately restore the release rate to within the above limit (s).
SURVEILLANCE REOUTREMENTS 3.4.1.1 The dose rate, due to noble gases in gaseous effluents shall be determined to be tithin the above limits in accordance with the methodology and parameters in Section 3.4.3 by obtaining representative camples and performing analyses in accordance with the sampling and analysis program specified in Table 3.4-1.
3.4.1.2 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'lua determined to be within the above limits in accordance with the methodology and parameters in Section 3.4.4 by obtaining representative samples and performing analyses in accordance l
with the sampling and analysis program specified in Table 3.4-1, i
l l
L CLINTON-1 3-4 Rev.6-12/89
' CPS-ODCM TABLE 3.4-1 RADIOACTIVE-GASEOUS WASTE SAMPLING AND ANALYSIS PROGRAM MINIMUM LOWER LIMIT OF SAMPLING ANALYSIS TYPE OF DETECTION (LLD)"
GASEOUS RELEASE TYPE FREOUENCY FREOUENCY' ACTIVITY ANALYSIS (uci/ml)
A. Station llVAC Wc,e gc,e Principal Gamma Emitters D 1x10 -4 Exhaust Grab Sample II-3 1x10 -6 B. Standby Gas W Principal Gamma Emitters b 1x10 -4 Treatment System Grab. Sample W Exhaust, when' flow exists 11 - 3 1x10-6 C. All release Types Continuous f W9 I-131 1x10-12 as Listed in A and Charcoal B above Sample I-133 1x10 -10 Continuous f W9 Principal Gamma Emittr rsD 1x10~11 Particulate (I .'.31, others)
Sample Continuous f M Grc.ss Alpha 1x10 -11 Composite Particulate Sample Continuous f Q Sr-89, Sr-90 1x10-11 Composite Particulate Sample CLINTOll-1 3-5 Rev.7-2/91
i CPS-ODCM -
T&BLE 3.4-1 (Continued)
RADIOACTIVE GASEOUS WASTE SAMPLING AND ANALYSIS PROGRAM TABLE NOTATIONS aThe LLD is-defined, for purposes of these specifications, as the smallest concentration of radioactive material in a sample that will-yield a net count, above system background, that will be detected with 95% probability with only 5% probability of falsely concluding that a blank observation represents a "real" signal.
For a particular measurement. system, which may include radiochemical separation:
4.66 sb LLD =
E x V x 2.22 x 10 6 x Y x exp (-Aat)
Where:
LLD is the "a priori" lower limit of detection as defined above, as microcuries per unit mass or volume, sb is the standard deviation of the background counting rate or of the counting rate of a blank sample as appropriate, as counts per minute, E:is the counting efficiency, as counts per disintegration, V is the sample size in units of mass or volume, 2.22 x 10 6 is the. number of disintegrations per minute per microcurie, Y-is the fractional radiochemical yield, when applicable, Ais,gheradioactivedecayconstantfortheparticularradionuclide (sec ) and At for plant effluents is the elapsed time between the midpoint of sample collection and the time of counting (sec).
Typical--values of E, V, Y, and at should be used in-the calculation.
II.should be recognized that the LLD is defined as an a griori (before the fact) limit representing the capability of a measurement system and not as an.g nosteriori (after the fact) limit for a particular measurement.
CLINTON-1 3-6 Rev.6-12/89
CPS-ODCM' TABLE 3.4-1 (Continued)
RADIOACTIVE GASEOUS WASTE SAMPLING AND ANALYSIS PROGRAM TABLE NOTATIOliS (Continued) bThe principal gamma emitters for which the LLD specification applies include the following radionuclides: Kr-87, Kr-88, Xa-133, Xe-133m, Xe-135, and Xe-138 in noble gas releases and-Mn-54, Fe-59, Co-58, Co-60, Zn-65, Mo-99, I-131, Cs-134, Cs-137, Co-141 and Ce-144 in iodine and particulate releases. This list does not mean that only these nuclides are to be considered. Other gamma peaks that are identifiable, together with those of the above nuclides, shall also be analyzed and reported in the Semiannual Radioactive Effluent Release Report pursuant to Specification 6.9.1.7 in the format outlined in Regulatory Guide 1.21, Appendix B, Revisio. 1, June 1974.
cSampling and analysis shall also be performed following shutdown, startup, or a THERMAL POWER change exceeding 15% of RATED THERMAL POWER within a 1-hour period.
d Not applicable.
" Tritium grab samples shall be taken at least once per 7 days from the ventilation exhaust from the spent fuel pool area, whenever spent fuel '
is in the spent fuel pool.
IThe 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 Sectiol.3 3.4.1, 3.5.1 and 3.5.2.
9Samples shall be changed at least once per 7 days and analysis shall be completed within 48 hours5.555556e-4 days <br />0.0133 hours <br />7.936508e-5 weeks <br />1.8264e-5 months <br /> after changing, or after removal from sampler.
Sampling shall also be performed at least once per 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> for at least 7 days following each shutdown, startup, or THERMAL POWER change exceeding 15% of RATED THERE'; POWER in 1-hour period and analyses shall be-completed within 48 hours5.555556e-4 days <br />0.0133 hours <br />7.936508e-5 weeks <br />1.8264e-5 months <br /> of changing. When samples collected for 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> are analyzed, the corresponding LLDs may be increased by a factor of 10. Twenty-four-(24) hour sampling requirements do apply if: (1) analysis shows that the DOSE EQUIVALENT I-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.
CLINTON-1 3-7 Rev.8-7/91
CPS-ODCM 3.4.2 Dose Rate Due to Noble Gases I In order to comply with Section 3.4.1.(a), the dose rate at or i beyond the site boundary due to noble gases shall be I calculated as follows*
Dt "EiKi((X/Q)mQim3 (1)
= total body dose rate at time of release, mren/ year Ds =ri(Li+1.1Mi) [ (X/Q)mQim] (2)
= skin dose rate at time of release, mrom/ year The turms in the above equations are defined in section 3.4.3.
3.4.3 Dose Rate Due To Radiciodines. Particulates and Tritium In order to comply with Section 3.4.1(b), organ dose rates due to radiciodines (I-131, I-133), particulates with half-lives
> 8 days and tritium shall be calculated as follows:
Do =riPij(X/Q)m im (3) .
t
) = organ dose rate at time of release, mrem /yr The terms used in equations (1) through (3) are defined as !
follows:
Ki = The total body dose factor due to gamma emitulonsforeachidentifiednobgegas radionuclide i, mrem /yr per gci/m Li.=
- The skin dose factor due to beta emissions for each identified goble gas radionuclide i, mrem /yr per gCi/m Mi = The air dose factor due to gamma emissions for each identified goble gas radionuclide i, mrad /yr per pCi/m (1.1 mrem / mrad converts air dose to skin dose)
CLINTON-1 3-8 Rev.6-12/89
CPS-ODCM Pij = The dose factor for non-noble gas radionuclide i and organ j.which includes pathway transport parameters, receptor usage factors and the dosimetry of the exposure. The dose factors fgr the inhalation, mrem /yr per pCi/m , pathway are listed in Table 3.4-3 (CHILD). Dose factors are based on NUREG-0133, Section 5.2.1.1 assumptions unless otherwise stated.
Qim = The release rate of noble gas radionuclide i in gaseous effluent from mixed-mode release points, pCi/sec Qim = The release rate of non-noble gas radionuclide i in gaseous effluent from mixed-mode release points, pCi/sec (3/Q)m = The highest calculated average relative concentration for any area at or beyond the sitegoundaryfrommixed-modereleases, sec/m Do is calculated for each of six organs and the total body; the maximum Do value is then used to determine compliance with Section T 3.4.1(b).
i The factors Ki, Li, and Mi relate the radionuclide airborne concentrations to various dose rates assuming a semi-infinite cloud.
These. factors are listed in Table 3.4-2 and were obtained from Table B-1ofRegulagoryGuide1.109aftermultiplyingthevaluesbythe conversion 10 pCi/pCi, 10CFR20 organ dose rate calculations are limited to the inhalation pathway only. Section 3.4.1(a) is anglicable to the unrestricted
'. area location characterized by the (X/Q)m value which results in the maximum total body or skin dose commitment. Should the total body and skin locations diffar, the selected location shall be that which minimizes allowable release rates.
There are unrestricted areas within the CPS site boundary which are utilized by members'of the public for residences, farming, recreation and camping. These areas are identified in Table 3.4-4.
Table 3.4-4 will be revised to remain consistent with the most recent land use census.
l CLINTON 3-9 Rev.6-12/89
CPS-ODL. -
TABLE 3.4-2 DOSE FACTORS FOR NOBLE GASES AND DAUGHTERS
- Total' Body . Gamma Air Beta Air Dose Factor. Skin Dose Factor Dose Factor Dose Factor
-Ki Li M i Ni Radionuclide (mrem /yr per pC1/m 3) (mrem /yr'per pC1/m 3) (mrad /yr per pC1/m 3) (mrad /yr per pCi/m 3)
Kr-85m 1.17E+03 1.46E+03 ,
1.23E+03 1.97E+03 Kr-85 1.61E+01 1.34E+03 1.72E+01 1.95E+03 Kr-87 5.92E+03 9.73E+03 6.17E+03 1.03E+04 Kr-88 1.47E+04 2.372+03 1.52E+04 2.93E+03 Kr-89 1.66E+04 1.01E+04 1.73E+04 1.06E+04 Kr-90 1.56E+04 7.29E+03 1.63E+04 7.83E+03 Xe-131m 9.15E+01 4.76E+02 1.56E+02 1.11E+03 Xe-133m 2.51E+02 9.94E+02 3.27E+02 1. 4 8E4 03 Xe-133 2.94E+02 3.06E+02 3.53E+02 1.05E+03 Xe-135m 3.12E+03 7.11E+02 3.36E+03 7.39E+02 Xe-135 1.81E+03 1.86E+03 1.92E+03 2.46E+03 Xe-137 1.42E+03 1.22E+04 1.51E+03 1.27E+04 Xe-138 8.83E+03 4.13E+03 9.21E+03 4.75E+03 Ar-41 8.84E+03 2.69E+03 9.30E+03 3.28E+03
- The listed dose factors are for radionuclides that may be detected in gaseous effluents.
CLINTON-1 3-10 Rev.6-12/89
CPS-ODCM-
, TABLE 3.4-3 INHALATION PATHWAY DOSE RATE FACTgRS (CHILD) -Pg i (mrem /yr per pCi/m ) '
QRGAN },DEE LIVER T. BODY THYROID EIDEEX lE GI LLI ISOTOPE H-3 NO DATA 1.12E+03* 1.12E+03 1.12E+03 - 1.12E+03 1.12E+03 1.12E+03 C 14 3.59E+04 6.73E+03 6.73E+03 6.73E+03 6.73E+03 6.73E+03 6.73E+03 NA-24 1.61E+04- 1.61E+04 1.61E+04 1.61E+04 1.61E+04 1.61E+04 1.61E+04
> P 32 2.60E+06 1.14E+05 9. 88 E+04 NO DATA NO DATA NO DATA 4.22E+04 CR 51 NO DATA NO DATA 1.54E+02 8.55E+01 2.43+01 1.70E+04 1.08E+03 MN-54 NO DATA 4.29E 04 9.51E+03 NO DATA 1.00E+04 1.58E+06 2.29E+04 HN-56 N0' DATA 1.66E+00 3.12E 01 NO DATA 1.67E+00 1.31E+0'4 1.23E+05 7.77E+03 NO DATA NO DATA 1.11E+05 2.87E+03 FE-55 4.74E+04 2.52E+04 2.07E+04 3.34E+04 1.67E+04 NO DATA NO DATA 1.27E+06 7.07E+04 FE 59 i
CO-58 NO DATA 1.77E+03 3.16E+03 NO DATA NO DATA 1.11E+06 3.44E+04 1.31E+04 2.26E+04 NO DATA NO DATA 7.07E+06 9.62E+04 CO-60 NO DATA 4.63E+04 2.80E+04 NO DATA NO DATA 2.75E+05 6.33E+03 NZ-63 8.21E+05 2.96E-01 1.64E 01 NO DATA NO DATA 8.18E+03 8.40E+04 NZ-65 2.99E+00 3.67E+04 );
CU-64 NO DATA 1.99E+00 1.07E+00 NO DATA 6.03E+00 9.58E+03 ZN-65 4.26E+04 1.13E+L 7.03E+04 NO DATA 7.14E+04 9.95E+05 1.63E+04 6.70E 02 9.66E 02 8.92E NO DATA 5.85E-02 1.42E+03 1.02E+04
- ZN 69 BR 83 NO DATA NO DATA 4.74E+02 NO DATA NO DATA ~ NO DATA LT 3.70E 15**
NO DATA 5.48E+02 NO DATA NO DATA NO DATA LT 3.70E-15 BR 84 -NO. DATA BR-85 NO DATA NO DATA 2'.53E+01 NO DATA NO DATA NO DATA LT 3.70EJ15 RD-86 NO DATA 1.98E+05 1.14E+05 NO DATA NO DATA NO DATA 7.99E+03 5.62E+02 3.66E+02 NO DATA NO DATA NO DATA 1.72E+01 RB-88 NO DATA RB-89 NO DATA 3.45E+02 2.90E+02 NO' DATA NO DATA NO DATA 1.89E+00 SR-89 5.99E+05- NO DATA 1.72E+04 NO DATA NO DATA 2.16E+06 1.67E+05 NO DATA 6.49E+06 N0' DATA NO DATA 1.4SE+07 S.43E+05 SR- 9 0 -' 1.01E+08 4.59E+00 NO DA'"A NO DATA 5.33E+04 1.74E+05 SR-91 1.21E+02 NO DATA-2.42E+05 SR-92: 1.31E+01 NO DATA 5.25E 01 NO DATA NO DATA 2.40E+04 2.62E+05 2.68E+05 )
Y-90 4.11E+03 NO DATA 1.11E+02 NO DATA NO DATA CLINTON 3-11 Rev.6-12/89
. - ,,- .. - - --. . - . . .-. . .~ .-. . .
' CPS-ODCM TABLE 3.4-3 (cont'd)
INHALATIONPATHWAYDOSERATEFACTgRS (CHILD) -Pp i (nrem/yr per pCi/m )
i QRGAN: 10HE LIVER T. BODY THYROID KIDNEY LIMG GI-LLI fSOTOPE Y 91m- 5.07E-01 NO DATA 1.84E-02 NO DATA NO DATA 2.81E+03 1.72+03 Y 91 9.14E+05 NO DATA 2.44E+04 No DATA NO DATA 2.63+06 1.84E+05 Y-92 2.04E+01 NO DATA 5.81E-01 NO DATA NO DATA 2.39E+04 2.39E+05 Y-93 1.87E+02 NO DATA 5.11E+00 NO DAI NO DATA 7.44E+04 3.89E+05 ZR 95- 1.90E405 4.18E+04 3,70E+04 NO DATA 5.96E+04 2.23E+06 6.11E+04 ZR 1.88E+02 2.72E+01 1.60E+01 NO DATA 3.89E+01 1.13E+05 3.51E+05 i
l NB-95 2.35E+04 9.18E+03 6.55E+03 NO DATA 8.62E+03 6.14E+05 3.70E+04 MO 99 NO DATA 1.72E+02 4.26E+01 NO DATA 3.92E+02 1.35E+05 1.27E+05 TC-99m 1.78E 03 3.48E-03 5.77E-02 NO DATA 5.07E 02 9.51E+02 4.81E+03 TC 101 8.10E-05 8.51E 05 1.08E-03 NO DATA 1.45E-03 5.82E+02 1.63E+01 RU-103 2.79E+03 NO DATA 1.07E+03 NO DATA 7.03E+03 6.62E+05 4.48E+04 RU-105 1.53E+00 NO DATA- 5,.55E-01 NO DATA 1.34E+0D 1.59E+04 9.95E+04
)
RU-106 1.36E+05 NO DATA 1.69E+04 NO DATA 1.84E+05 1.43E+07 4,29E+05 AG-110m 1.69E+04 1.14E+04 9.14E+03 NO DATA 2.12E+04 5.48E+06 1.00E+05 TE 125m 6.73E+03 2.33E+03 9.14E+02 1.92E+03 NO DATA 4.77E+05 3.38E+04 TE 127m 2.49E+04 8.56E+03 3.03E+03 6.07E+03 6.36E+04 1.48E+06 7.14E+04
-TE 127 2.77E+00 9.51E 01 6.11E-01 1.96E+00 7.G7E+00 1.00E+04 5.62E+04 TE 129m- 1.92E+04 6.85E+03 3.04E+03 6.33E+03 5.03E+04 1.76E+06 1.82E+05 TE-129 9.77E-02 3.50E-02 2.38E-02 7.14E-02 2.57E 01 2.93E+03 2.55E+04 TE-131m 1.34E+02 5.92E+01 5.07E+01 9.77E+01 4.00E+02 2.06E+05 3.08E+05 TE-131 2.17E-02 8.44E 03 6.59E-03 1.70E-03 5.98E 02 2.05E+03 1.33E+03 TE-132 ~ 4.81E+02 2.72E+02 2.63E+02 3.18E+02 1.77E+03 3.77E+05 1.38E+05 I-130- 8.18E+03 1.64E+04 8.44E+03 1.85E+06. 2.45E+04 NO DATA 5.11E+03 1-131' 4.81E+04 4.81E+04 2.73E+04 1.62E+07 7.88E+04 NO DATA 2.84E+03 I-132 2.12E+03 4.07E+03 1.'88E+03 1.94E+05 6.25E+03 NO DATA 3.20E403 I-133 1.66E+04 2.03E+04 7.70E+03 3.85E+06 3.38E+04 NO DATA 5.48E+03 I-134 1.17E+03 2.16E+03 9.95E+02 5.07E+04 3.30E+03 NO DATA 9.55E+02
)
CLINTON-1 3-12 Rev.6-12/89
CPS-0DCM' TABLE 3.4-3 (cont'd)
INHAI.ATIONPATHWAYDOSERATEFACTgRS (CHILD)
Pj i (mrem /yr per NCi/m )
L.E!Dy TiPIROID RIDNEY M11Q OI.LLI QRGANi HDE LIVER ISOTOPE 8.73E+03 4.14E+03 7.92E+05 1.34E+04 NO DATA 4.44E+03 I.135 4.92E+03 1.21E+05 3.84E+03 CS.134 6.51E+05 1.01E+06 2.25E+05 NO DATA 3.30E+05 1.71E+05 1.16E+05 NO DATA 9.55E+04 1.45E+04 4.18E+03 j CS.136 6.51E+04 1.28E+05 NO DATA 2.82E+05 1.04E+05 3.62E+03 CS.137 9.07E+05 0.25E+05 5.55E+02 NO DATA 6.21E+02 6.81E+01 2.70E+02 CS.138 6.33E+02 8.40E+02 5.37E 02 NO DATA 8.62E.04 5.77E403 5.77E+04 BA-139 1.84E+00 9.84E.04 y
6.48E401 4.33E403 NO DATA 2.11E401 1.74E 06 1.02Et05 BA 140 7.40E+04 2.75E+02 1.96E.01 1.09E.04 6.36E.03 NO DATA 9.47E.05 2.92E+03 BA.141 2.74E+00 3.60E.05 2.79E.03 NO DATA 2.91E.05 1.64E+03 BA 142 -
- 00E 61 7.55E+01 NO DATA No DATA 1.83E+05 2.26E+05 1.A.140 6.44E+02 2.25E+02 1.29E.01 NO DATA NO DATA 8.70E+03 7.59E+04 1A 142 1.30E+00 4.11E.01 2.90E+03 NO DATA 8.-55E+03 5.44E+05 5.66E+04 CE.141 3.92E+04 1.95E+04
)
2.88E+01 NO DATA 8.36E+01 1.15E+05 1.27E+05 CE;143 3.66E+02 1.99t+02 3.62E+05 'NO DATA 1.17E+06 1.20E+07 3.89E+05 CE.144 6.77E+06 2.12E+06 9.14E+02 NO DATA 3.00E+03 4.33E+05 9.73E+04 PR 143 1. 85E444 5.55E+03 3.00E 03 NO DATA 9.77L.03 1.57E+03 1.97E+02 PR.144 5.96E.02 1.85E.02 6.81E+02 NO DATA 4.81E+03 3.28E+05 8.21E+04 ND.147 1.08E+04 8.73E+03 4.33E+00 NO DATA NO DATA 4.11E404 9.10E+04 V 187 1.63E+01 9.66E+00 2.35E+01 NO DATA 9.73E+01 5.81E+04 6.40E+04 NP.239 4.66E+02 3.35E+01 i
~ *1.12 x 10J o*Less than 3.70 x 10*!.5 L
CLINTON-1 3-13 Rev.6-12/89 g.- w - ,- m - .r, -- -, -w,
- * 'emec .sw-.=w yw ..,y --w w-r..,=--.,w,m+.7, m =.*w---er- + vee ng ..g-, ,-t % p g- p-m q t--m.e.g,
CPS-ODCM l
TABLE 3.4-4 1hCATION OF MEMBERS OF Tile PUBLIC VITilIll Tile CPS SITE BOUNDARY AND TilEIR ASSOCIATED OCCUPANCY FACTORS
- distance Occupancy Location (mile / motor) Sector (hrs /vri Road 0.3/495 SE 243(1)
Agri-cultural Acreago (2) 0.9/1372 SSW 964(3)
Clinton Lako 0.2/335 NW 2208(4)
Department of Conser-vation Recreation Area 0.8/1287 ESE 2208(5)
Residence 0.8/1219 SW 8760 Residenco 1.5/2414 -Wst? 8760 Residence 1.7/2736 SSE 8760 (1) Assu[nos travel on road for forty minutos por day.
(2) Maximula farm acreage (276) within site boundary.
(3) Assumes 3.5 hours5.787037e-5 days <br />0.00139 hours <br />8.267196e-6 weeks <br />1.9025e-6 months <br /> in field per acro farmed.
(4) Assumes continuous occupation on Clinton Lake for the months of June, July, and August.
(5) Assumes continuous occupation on Department of Conservation camping areas for the months of June, July, and August.
- Dosas for such MEMBERS OF THE PUBLIC are provided in the Semiannual Radioactive Effluent Release Report as given in Section 6.3.2.
CLINTON-1 3-14 Rev.6-12/89
....=.w.
CPS-ODCM 3.5 10CFR50. APPENDIX I L RELEASE RATE LIMITS The Operation and Surveillance Requirements concerning 10CFR50 (Appendix I) Release Rate Limits are specified in Sections 3.5.1 and 3.5.2 as follows. Dose calculations for ensuring compliance with these limits are discussed -
in Sections 3.5.3 and 3.5.4.
3.5.1 Noble Gas Dose - Operation and Surveillance Requirements ,
Qfg ATION REQUIREMENT The air dose due to noble gases released in gaseous effluents, from each reactor unit, to areas at and beyond the SITE BOUNDARY (see Figure 3.1-1) chall be limited to the following
-a. During any calendar qi3arter: 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 yeart Less than or equal to 10 mrads for gamma radiation and less than or equal to 20 mrad for beta radiation.
This requirement applies at all times.
REMEDIAL REOUGEMENT:
- a. With the calculated air dose from radioactive noble gases in gaseous affluents ex:eeding any of the above limits, in lieu of a Licensee Event Report, prepare and submit to the Regional Administrator of the Regional Office of the NRC within 30 days 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.
SURVEILLANCE REOUTREMENTS 3.5.1.1 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 described in Section 3.5.3 ct leant once per 31 days.
l l
l l
CLINTON-1 3-15 Rev.6-12/89 l
1 CPS-ODCM 3.5.2 Iodine-131, Iodine-133, Tritium, and Radionuclides in Particulate Form - Operation and Surveillance Requirements OPEFATTON REOUTRFMENT The dose to a MEMBER OF THE PUBLIC from iodine-131, iodine-133, tritium, and all radionuclides in particulate form with half-lives greater thsn 8 days in gaseous effluents released to areas at and beyond the SITE
, BOUNDARY (see Figure 3.1-1) shall be limited to the following:
- a. During any calendar quarter: Less than or equal to "- A mrems to any organ, and
- b. During any calendar year: Less than or equal te 15 mrems to any organ.
This requirement applies at all times.
BEMEDIAL REOUIREMENT:
- a. With the calculated dose from the release of iodine-131, icdine-133, tritium, and radionuclides in particulate form with half lives greater than 8 days, in gaseous affluents exceeding any of the above limits prepare and submit to the Regional Administrator of the Regional Office of the NRC within 30 days a Special Report that identifies the cause(s) for exceeding the limit and defines the corrective actions that have been taken to reduce the releases and
) the proposed corrective actions to be taken to assure '. hat subses ont releases will be in compliance with the above limits.
SURVETLTANCE REOUTREMENTS 3.5.2.1 Cumulative dose contributions for the current calen'dar 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 motb;,Mlogy and parameters in Section 3.5.4 at least once por 31 days.
CPS-ODCM 3.5.3 N_oble Gas Air Dose Ecuations The air dose at or beyond the sito boundary due to noble gases released in gaseous effluent vill be determined using the following ,
equations.
3.5.3.1 During any calendar quarter or calendar year, for gamma radiation:
D7 = 3.l'i x 10-8 EMii (X/Q)n Qim (4) 3.5.3.2 During any calendar quartor or calendar year, for bota radi6 tion:
Dp = 3.17 x lo-B ri Ni (X/Q)m Oim (5)
Where Mi= The gamma air dose f actor for each identified noble gas radionuclide i, mrad /goarpor pCi/m (Mi values aro listed in Table 3.4-2).
Ni= The beta air dose factor +
i for each identified noble gas radionuclide i,3 mrad / year por 4Ci/m (Ni values are listed in Table 3.4-2).
(E76)m = The highest calculated average relativo -
concentration from mixed-modo roloaso points for areas at or beygnd the site boundary, soc /m The average releano of Qin = noble gas radionuclido i for long-term releases from mixed-modo release points, pCi. Rolaasos shall be cumulativo over the "
calendar quarter or year, as appropriate.
3.17 x 10-8 = The inverso of the number of seconds in a year.
CLINTON-1 3-17 Rev.6-12/89 I
CPS-0DCM Section 3.5.1 noble gas deso
- calculations are evaluated at the oito boundary location whors maximum .
air dosos provail. Should the beta and gamma locations differ, the selected location shall be that which minimizes allowable rolcaso ratos due to the gamma component.
3.5.4 Radiciodines. Particulates and Tritium Dose Equations The done to an individual at or beyond the oito boundary due to radiciodinos (I-131, I-133), tritium and particulates with half-lives > 8 daye, will be datormined using the following equation:
for any et'*adar quarter or calendar year, D p = 3.17 x . qR s r.
Wm im (6) whero 64m = The rolettsos of radionuclide 1 (I-131, I-133,
^
tritium .$nti particulates) for relonces from mixed-modo releano points, pC1. Releasas shall be cumulativo over the calendar quarter or year, asLappropriato. .
)
ll (D/Q)m = The relative deposition from mixed-modo roloaso pojntsforareasatorPsyondthesiteboundary, m
Wm = The dispersion paramotor for estimating the dose to an individual at a controlling location for mixed-mode releases.
=
_ (X/Q)m, soc 3/m , for the inhalation pathway
= (D/Q)m, m-2, for the food and ground plano pathways 3.17 x 10-8 = The inverse of the number of seconds in a year.
R aij =
Thedosefactorforeachidenti{iedradionuclide i, age group (a) and organ j , p mrom/yoar por pCi/ soc or mrem / year por pC1/m I
CLINTON-1 3-18 Rev.6-12/89 ,
. l
. . - -,,-v...- -,.,v. - -.,r. - - . , . - - . . . - , _ . . _ , . _ . - . , . . , . _ . . . , . , . . _ . ,m, . ..
CPS-0DCM Section 3.5.2 is applicable to the location at or beyond the site boundary where the combination of existing pathways and receptor age groups indicates the maximum potential exposure. The inhalation and ground ,
plane exposure pathways exist at all locations; other pathways exist as determined by the most current land use census.
3.5.4.1 Dose Factor For Radionuclide 1 (R a1] ..)
The Raij values used to calculate D in equation (6) are determined separately for eEch of the potential exposure pathways, namely:
- Inhalation (I)
- Ground Plane Contamination (G)
- Grass-Cow / Goat-Milk (C)
- Grass-Cow-Meat (M) e
- Vegetation (V)
The Ra14 parameter is independent of the duration of gaseous releases and is calculated using the methodology discussed in the remainder of this section.
3.5.4.1.1 Calculation of the Inhalation Eathway Factor. R ..
ax) 3 R 13= K'(BR)a (DFA1 )a, mrom/ year per pCi/m (7) )
where 6 K' = A units conversion constant, 10 pci/yci e of the receptor (BR)a=Thebreathingrag/
age group (a), m year.
= 1400 (infant)-
= 3700 (child)
= 8000 (teen and adult)
Values for (BR)a are obtained from NUREG-0133, p.32.
(DFA1 )a=
The organ inhalation dose factor for I receptor of age group (a) for radionuclide i, mrem /pCi. Values were obtained from for (DFAEi)athrough Tables 7 E-10 of )
Regulatory Guide 1.109 and are i presented in Tables 3.5-1 through 3.5-4 of this manual, i l
3-19 Rev.6-12/89 CLINTON-1
CPS-ODCM 3.5.4.1.2 Calculation of the Ground Plane Pathway Factor R t
Rf
= K'K" (SF) (DFG i ) (1-0 "Al )/Ai
, (8) m2 -mrem / year por pCi/coc where K' = A units conversion constant, 10 6 peijpei X" = A units conversion constant, 8760 hour0.101 days <br />2.433 hours <br />0.0145 weeks <br />0.00333 months <br /> / year SF = The shielding factor, dimensionless
= 0.7 as suggested in Table E-15 of Regulatory Guide 1.109 l
DFG1= The ground plane dose conversion factor fog radionuclide i, mrem / hour per pCi/m . Values for DFGi were obtained from Table E-6 of Regulatory Guide 1.109 and are
( presented in Table 3.5-5 of this
' ) manual.
! A1= The decgy constant for radionuclide i, see t= The exposure time, sec
= 6.31E+08 sec (20 years) 3.5.4.1.3 Calculation of'The' Grass-Cow / Goat-Milk Pathway Factor. R ..
al]
C R,g = K' Qp(U gp) F m (r) (DFLi )a (9)
Ag + Aq ff p3 (1-fp3f )o-Ai th e-Ait f, Y Y s
p m 2 -mrem /yr per pCi/sec CLINTOH-1 3-20 Rev.6-12/89
,p---r. > , - - - p. -y e, 4., ,, - r . , . - _ . - , . . . - - . . - . . - . r. c--. r-., .....-m..---x,- -
.v.., .-wr, ,.ry- -- ,
CPS-ODCM where K' = A units conversion constant, 10 6 pci/pci Qp = The cow / goat feed consumption rate, kg(vet)/ day U ap = The receptor's milk consumption rate for age group (a), liters / year Yp = The agricultural productivity by unit ar a f Pasture feed grass, kg/m 2 Ys=Theagriculturalproductivitygy unit area of stored feed, kg/m Fm =coefficients, The stable element transfer days / liter r = Fraction of deposited activity retained on feed grass, dimensionless (DFLi )a = The organ ingestion dose factor for radionuclide i and the receptor in age group (a) , mrem /pci. Values for (DFL ) }
Tables E 1$through were obtained E-14 of from Regulatory Guide 1.109 and are presented in Table 3.5-6 through 3.5-9 of this manual.
A 1 = The decgy constant for radionuclide 1, sec Ay= The decay constant for removal of activity on leaf an byweatnering,sec~gplantsurfaces
= 5.73 x 10~7 sec ~1 (corresponding to a 14-day half-life) t g = The transport time from pasture to animal, to milk, to receptor, soc t h = The transport time from pasture to ha rvest, to animal, to receptor, sec C2dNTON-1 3-21 Rev.5-2/89
' ~ ' ' " * - _y , , . ,
CPS-0DCM l f p
= Fraction of the year that the cow / goat is on pasture, dimensionless f
3
= Fraction of the cow / goat feed that is pasture grass while the cow / goat is on pasture, dimensionless Tgeinputparamotorsforcalculating R,g are listed in Table 3.5-10.
Tritiun The concentration of tritium in milk is based on its airborne concentration rather than the deposition.
C RT = K'K"F O Um F ap(DFL1 )a (0.75(0.5/H)],
mrem /yr per pci/m 3 (10) where K" = A units convgrsion constant, 10 gm/kg
) 11 = The absoluto atmospheric humidity
= 8 gm/m 3 (ITUREG-013 3, p. 34) 0.75 = The fraction of total feed that is water, dmencionless 0.5 = The ratio of the specific activity of the food grass water to the atmospheric water, dimensionless The other parameters arg as defined in the calculation of R CLINTON-1 3-22 Rev.5-2/89
CPS-ODCM ,
g.arbon - 14 4
Following the development of equation C-8 on page 1.109-26 of Regulatory Guide 1.109, carbon-14 is assumed to be released as an oxide, either C 14 0 or C 14 0 2 The concentration of carbon-14 in milk is therefore based upon its airborne concentration assuming that the vegetation C14/C ratio is the same as the local atmospheric C 14 /C ratio.
RC4 = K'K"Fm O fUap(DFL1 )a P(0.11/0.16), mrem /yr per 4Ci/m3 (11) where p = Fractional equilibrium ratio, dimensionless
= Ratio of the total annual C-14 atmosheric release time to the total annual photosynthesis time (4400 hours0.0509 days <br />1.222 hours <br />0.00728 weeks <br />0.00167 months <br />) not to exceed unity
= 1.0 0.11 = Natural carbon fraction of total plant mass, dimensionless
)
0.16 = Atuogheric natural carbon concentration, qu/m >
The other parameters are as defined in the calculation of R C M
3.5.4.1.4 Calculation of The Grass-Cow-Meat Pathway Factor. R aij Raij " K#O F(Uap) Fg (r) (DFL1 )a ff ps (1~fpsf ) e-Al th (e~Ait s),
Ai+Ay Yp Y3 m 2 -mrom/yr per pCi/sec (12) where K'- =
A units convgrsion pCi/gCi constant, 10 U gp =- The receptor's meat consumption rate for age group (a), kg/ year Ff = The stable element transfer coefficient, days /kg CLINTON-1 3-23 Rev.6-12/89
, . .,- - ~ - - , . . - - - . . .~ .-_---.L _- - - . - - - - - - - -
CPS-ODCM ts = The transport time from slaughter of meat animal to receptor, seconds ;
tg = The transport time from crop field to receptor, seconds l (DFLi )a= The organ ingestion dose factor for radionuclido i and the receptor in age group-(a), mrem per pci. ,
Values are tabulated in !
Table 3.5-6'through 3.5-9 of this Manual.
The: input parameters necessary for calculating R are listed in Table 3.5-11. -AllOkkertermsareas defined for equations (9) and (10).
Tritium:
The concentration of tritium in meat'is based on
'its airborne concentration rather than the
. deposition.
' M RT= K'K"FgQyU ap(DFLi )a (0.75(0.5/H)) _ , mram/yr por-
- Ci/m 3 (13) ;
The terms in equation-(13) are as defined in equations ,
(10) and-(12). ,
carbon - 14 JFollowing the development of_ equation C-8 on page
. 1.109-26 of Regulatory Guide 1.109, carbon-1g4 is aggumed to-be released as an oxide,'either C .0 or C 0. 2 .The concentration of carbon-14 in meat-is therefore~basedupon-itsairbo{neconcentration ion C /C ratio is the same as assumingthatthevegetgg/Cratio.
=the local atmospheric c 3
.R$4=- K'K"F g Qg U ap(DFL i ) a p(0.11/0,16) , mrum/yr per 'pci/m - '(14)
The terms-in equation (14) are as defined in equations-(11) and.(13).
CLINTON 3-24 Rev.1-11/85~
4.
4- c - . . - ..- -. , . . - - . . . , . , _ . . - , - - . . . . _ . - _ . , _ _ . . - . _ . - . . ,
. - - . , . , _ . ~ _ . ,
CPS-ODCM 3.5.4.1.5 Calculation of the Vecetation Pathway Factor. R 33 ;
- U f e~Al tL + U ag f e-Ai th ,
R y = K' (DFLi )a L Yv( Ai+Aw) m2 -mrem /yr per 4C1/sec (15) ,
where K' = A units convgrsion pci/pci constant, lo L = The consumption rate of Ua fresh leafy vegetation by
- the receptor in age group (a), kg/yr S
Ua = The consumption rate of stored vegetation by the receptor in age group (a),
kg/yr ft = The fraction of the annual intake of fresh leafy vegetation grown locally, I!
dimensionless f
I
= The fraction of the annual intake of stored vegetation grown locally, dimensionless tg = The average time between harvest of leafy vegetation and its consumotion, seconds tg = The average time between harvest of stored vegetation and its consumption, seconds Yy= The vegetatiog areal density, kg/m l
CLINTON-1 3-25 Rev.6-12/89
. ~
l CPS-ODCM (DFL1 )a= The organ ingestion dose factor for redionuclide i and the recs ~ '.or in age group (a), mrem per pC1.
Values are tabulated in Table 3.5-6 through 3.5-9 of this Manual.
The input parameters necessary for calculatingRfigarelistedinTable 3.5-12. All other terms are as defined for equations (9) through (14).
Tritium:
The concentration of t'ritium in vegetation is based on its airborne concentration rather than the deposition.
R = K'K"(U faL+Uf) g (DFL i )a (0.75(0.5/H)]
mrem /yr per #Ci/m 3
. (16)
The terms in equation (16) are as defined in
) equations (10) and (15).
Carbon-14 Following the development of equation C-8 on page 1.109-26 of Regulatory Guide 1.109, carbon-Ig4 1s assyged 0
to be released as an oxide, either C 0 or C 2 The concentration of carbon-14 in vegetation is therefore based upon its airborne conggntration assuming that the vegetation.C atmospheric C fCratioisthesameasthelocal
/C ratio.
R 4
=
K'K"(U faL+Uf) ag (DFLi )a P(0.11/0.16), (17) arem/yr per 4C1/m 3 The terms in equation (17) are as defined in equations (11) and (15).
I C V H The pathway dose rate factors (Raij, Raij, Raij, R aij' Rf), by age group, are listed in Table 3.5-13 through 3.5-31.
CLINTON-1 3-26 Rev.1-11/85 f ,..- - , . , - - . . -_ . - - -
c CPS-ODCM 3.6 Gaseous Radwaste (Offcas Treatment) f 3.6.1 Gaseous Radwaste (Offgas Treatment) System - Operation and i Surveillance Requirements QEERATION REOUIREMENT !
I l
The GASEOUS RADWASTE (OFFGAS) TREATMENT SYSTEM shall be in operation. This requirement applies whenever the main condenser eteam jet air ejector system is in operation.
REMEDIAL REOUIREMENT:
- a. With gaseous radwaste from the main condenser air ejector l system being discharged without treatment for more than 7 !
days, prepare and submit to the Regional Administrator of the j Regional Office of the NRC within 30 dayr a Special Report l that includes the following information:
- 1. Identification of any inoperable equipment or subsystems, and the reason for the inoperability. l
- 2. Action (s) taken to restore the inoperable equipment to OPERABLE status, and
- 3. Summary description of action (s) taken to prevent a recurrence. . .
SURVEILLANCE REOUIREMENTS )
3.6.1.1 The GASEOUS RADWASTE (OFFGAS) TREATMENT SYSTEM shall be verified to be in operation once every 12 hours1.388889e-4 days <br />0.00333 hours <br />1.984127e-5 weeks <br />4.566e-6 months <br /> when the main '
condenser air ejector is in use to ensure that the main condenser offgas treatment system is functioning.
NOTE Prior _to placing the Offgas Treatment System in the charcoal bypass mode, the alarm setpoints for the Station HVAC Exhaust and the Post-Treatment Offgas radiation monitors shall be calculated to cccount for the increased fractions of short-lived noble gases.
The noble gas release fractions shall be based either on actual reasured values or_on design basis noble gas concentration fractions-(30-minuto delay) in the primary coolant offgas, j
CLINTON-1 3-27 Rev.6-12/89
CPS-ODCM 3.7 Vant11ation Exhaust Treatment 3.7.1 Ventilation Exhaust Treatment System - Operation and Surveillance Requirement OPERATION REOUTREMENT The VENTILATION ZXHAUST TREATMENT SYSTEM (VI:TS) shall be used to reduce radioactive materials in gaseous waste prior to their discharge when the projected doses due to gaseous effluent releases to areas at and beyond the SITE BOUNDARY (see Figure 3.1-1) would cxceed 0.3 mrem to any crgan in a 31-day period. This requirement applies at all times other than when-the VETS is undergoing routino maintenance.
REMEDIAL REQUIREMENT:
- c. With gaseous waste being discharged without treatment and in excess of the above limit, prepara and submit to the Regional Administrator of the Regional Cffice of the NRC within 30 days a Special Report that includes the following information:
- 1. Explanation of why gaseous radwaste was being discharged without treatment, 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.
4 SURVEILLANCE REOUTREMENTS _
3.7.1.1 Doses due to gaseous releases from the_ site shall be projected at least once per 31 days in accordance with this manual when the ventilation exhaust treatment system is not in use.*
- 3. 7 ; 1. 2 - The installed VENTILATION EXHAUST TREATMENT SYSTEM shall be considered OPERABLE by meeting the Operation Requirements of Sections 3.4, 3.5.1, and 3.5.2.
- The projected doses resulting from such releases will be calculated using Section 3.5.4 methodology. If the dose impact resulting from the projected 31-day release exceeds 0.3 mrem and the VETS is capable of 1
reducing the. projected impact to less than 0.3 mrem, the VETS shall be used.
. CLINTON-1 3-28 Rev.6-12/89
l CPS-ODCM 3.8 Effluent Monitor Setroint Calculations GOseous affluent Process Radiation Monitor (PRM) alarm setpoints chall be calculated to ensure that the dose rate in unrestricted creas due to noole gases released do not exceed 500 mrom/ year to the total body and 3000 mrom/ year to the skin. The initial cctpoints were calculated using the DWR-GALE code radionuclide mix cbtained for CPS 1 when the actual radionuclide mix can be dstermined, it will be used for setpoint calculations. The PRM cctpoints are based on the instantaneous noble gas dose rates and cre applied at the point of which the effluent enters an unrestricted area.
Due to PRM limitations, non-noble gas setpoints will not be IUplemented to demonstrate compliance with Section 3.4.l(b).
Compliance with the organ dose rate limitation is demonstrated during performance of sampling and analysis activities required by TObie 3.4-1.
Both total body and skin dose setpoints will be calculated and the t0re restrictive limit applied to the respective PRM. The actual ,
cotpoint used may be lower than the restrictive limit since the two rolease points will-be partitioned such that their sum does not exceed 100 percent of the restrictive limit. The percentages used to partition the release points could vary at plant discretion to cccommodate plant operational conditions. In no case will the c:mbined releases due to variations in the PRM setpoints result in offluent limits being exceeded.
3.8.1 Total Body Dese Rate Settoint )
t The fraction of the total gaseous radioactivity in each gaseous effluent release path j for each noble gas radionuclide i shall be determined using the following relationships fj=Cj i
i , dimensionless (18)
ECj ii where L Cj=
i The measured concentration of identified noble gas radionuclide i in gaseous effluent release path j, l
pCi/cc l The maximum acceptable release rate of all noble gases in releaso path j to cemply with Section 3.4.1 is calculated by using the equation:
Qj=
T 500 F 3
, pCi/sec (19)
(X/Q)3ri(Kiif j)
CLINTON-1 3-29 Rev 6-12/89
j CPS-oDCM where Qj=
T The maximum acceptable release rate of all noble gases in release path j, pCi/sec Fj = Total dose rate allocation factor assigned to release path j (varying between 0.0 and 1.0), dimensionless 500 = Total body dose rate limit specified in section 3.4.l(a), mrem / year The highest calculated (X/Q)3= average relative concentration of release path j at the site boundary Ki ,= The total body dose factor dLe to gamma emissions of noble gas radionuclide i as listed in Table B-1 of Regulatory Guide 1.109 and Table mrom/yr per pCi/m 3.4-2ofthjsmanual,
)
fg= The fractiott as defined by i
equation (18),
dimensionless The total maximum acceptable concentration setpoint of noble gas radionuclides in release path j is calculated using the following equation:
C;j = OT j , pCi/cc (20)
R where Cj=T The total maximum acceptable concentration setpoint of all noble gases in release path j, uCi/cc CLINTON-1 3-30 Rev.6-12/89 f
CPS-CDCM 1 Qj=
T The maximum acceptable release rate of all noble gases in release path j determined from equation (19), #Ci/sec R4=
The effluent release rate ,
of release point j, cc/sec 3.8.2 Ehin Dese Rate SetDoint To ensure compliance with the Section 3.4.1(a) skin dose rate limit, PRM setpoints shall be calculated using the nethodology presented in section 3.8.1 and by substituting the following equation for equation (19):
.Qgj = 3000fj , #Ci/sec (21)
(X/Q)3ri(Li+1.1M1 ) fi j where
= Th's maximum acceptable release rate Q33 of all noble gases in release path j, #Ci/sec Fj = Total dose rate allocation factor assigned to release path j (varying between 0.0 and 1.0), dimensionless 3000 = Skin dose rate limit specified in Section 3.4.1(a) , mrem / year (X/Q)3 = The highest calculated average relative concentration of release path j at the site boundary Li = The skin dose factor due to gamma ,
emissions for each identified noble '
gas rgdionuclide=1, mrem /yr per
- Ci/m , as listed in Table 3.4-2 of this Manual.
1.1 = An air dose to skin done equivalent conversion factor, mrem / mrad Mi = The air dose factor due to gamma emissions for each identified noble gas rgdionuclide.1, mrad /yr por
- Ci/m , as listel in Table 3.4-2 of -
i this Manual l
CLINTON-1 3-31 Rev.6-12/89
,yr,-,. y- r ,,-w 4. , , ,e.-n .. m ,, , ,. _
.-W. . , , _ -- - - _ _ - _.--v.- - - - , , - m - ..
CPS-ODCM
- fg i
= The fraction defined by equation (18)
The calculated total body and skin maximum acceptable concentration setpoints are compared and the more restrictive setpoint used. A cafety factor may also be applied to the concentration setpoint calculated by equation (20) to compensato for statistical fluctuations and measurement errors.
Y x
)
r CLINTON-1 3-32 Rev.5-2/89
CPS-ODCM ,
3.9 Radioactive Gaseous Monitorino Instrumentation 3.9.1 Offgas Radiation Monitoring Instrumentation - Operation and Surveillance Requirements OPERATION REOUTREW yT g.,
The offgas radiatios monitoring instrumentation channels shown in Table 3.9.1-1 shall be. OPERABLE, with their alarm / trip notpoints within the specified limits. This requiremont applies during operation uf the main condonner air ejector (s).
REMEDIAL REOUIREMENT!
- a. With a radiation monitoring instrumentation channel alarm / trip setpoint exceeding the value shown in Tablo 3 9.1-1, adjust the setpoint to within the limit within 4 hours4.62963e-5 days <br />0.00111 hours <br />6.613757e-6 weeks <br />1.522e-6 months <br /> or dociare the channel inoperable.
- b. With one or more radiation monitoring channels inoperable, comply with the REMEDIAL REQUIREMENT specified by Table 3.9.1-1.
SURVEILLANCE REOUIREMENTS 3.9.1.1 Each of the above required radiation monitoring instrumentation channels shall be demonstrated OPERABLE by the parformance of the CHANNEL CHECK, SOURCE CHECK, CHANNEL FUNCTIONAL TEST and CHANNEL CALIBRATION at the frequencies shown in Tcble 3.9.1-2.
)
4 l
l-CLINTON-1 3-33 Rev.6-12/89 i
e CPS-ODs n TABLE 3.9.1-1 OFFGAS RADIATION MONITORING INSTRUMENTATION MINIMUM CIIANNELS ALARM / TRIP REMEDIAL l REOUIREMENT INSTRUMENTATION OPERABLE # SETPOINT
- 1. Pre-treatment Off-gas 1(b) $ 50 pCi/cc***6 5 PRM - Noble Gas Activity Monitor
- 2. Post-treatment Off-gas PRM
~
- a. High-Range Noble l IDI i 7.06 pCi/cc @
h 6 Gas Activity Monitor Providing Alarm and Automatic Termina-tion of Release
- b. Effluent System -
1 NA 7 Flow Rate Measuring Device
- c. Sample Flow Rate 1 NA 7 Measuring Device l
I CLINTON-1 3-34 Rev.6-12/89
CPS-ODCM ZABLE 3.9.1-1 (Continuedi i
OFFGAS RADIATION MONITORING INSTRUMENTATION l 1
TABLE NOTATIONS
- Alarm only. l f A channel may be placed in an. inoperable status for up to 1 hour1.157407e-5 days <br />2.777778e-4 hours <br />1.653439e-6 weeks <br />3.805e-7 months <br /> for the purpose of performing surveillances.
l
$ Reactivity concentration expected at the monitor location is !
a noble gas mix with a 2.9-minute decay.
$$ Radioactivity concentration expected at the monitor location is a noble gas mix released from the off-gas treatment system.
(b) Channel OPERABILITY shall include the capability of either I the Main Control Room Centrr.1 Control Terminal (MCR-CCT) or the Radiation Protection Off k,e Central Control Terminal (RP-CCT) to provide the alarm status of the applicable radiation monitor channel (s).
REMEDIAL VOUIREMENT REMEDIAL REQUIREMENT a. With both the MCR-CCT and RP-CCT 5 inoperable, .
);
- 1. Perform a CHANNEL CHECK using local monitor indication within 8 hours9.259259e-5 days <br />0.00222 hours <br />1.322751e-5 weeks <br />3.044e-6 months <br /> and at least once per 8 hours9.259259e-5 days <br />0.00222 hours <br />1.322751e-5 weeks <br />3.044e-6 months <br /> thereafter, and
- 2. Rostore the MCR-CCT or RP-CCT to OPERABLE status for the applicable channel (s) within the next 30 days, and if unsuccessful, prepare and submit to the Regional Administrator of the Regional Office of the -
NRC within the next 10 days a Special Report outlining the cause of the CCT failure or malfunction and the action taken to restore the inoperable equipment to OPERABLE status.
- b. With the Pre-treatment Off-gas PRM - Noble Gas Activity Monitor otherwise inoperable, gases from the main condenser off-gas treatment system may be released to the environment provided:
- 1. The off-gas treatment system is not bypassed, '
and i
CLINTON-1 3-35 Rev.6-12/89
,m. _ . . . . . - ,
~ m,i...w.,r. - - , . _ , . . . ,_w e , . . , . . , , , . . , . , -
- m. _ ,
I CPS-CDCM 1
TABLE 3.9.1-1 (Continued)
OFFGAS RADIATION MONITORING INSTRUMENTATION TABLE NOTATIONS
- 2. The post-treatment air ejector off-gas PRM high range noble gas activity monitor is ,
OPERABII, or the provisions of REMEDIAL l REQUIREMENT 6-b are in effect, and ;
- 3. Grab canples are taken at least once per 8 hours9.259259e-5 days <br />0.00222 hours <br />1.322751e-5 weeks <br />3.044e-6 months <br /> and analyzed for gross noble gas :
activity within 4 hours4.62963e-5 days <br />0.00111 hours <br />6.613757e-6 weeks <br />1.522e-6 months <br />.
REMEDIAL REQUIREMENT a. With both the MCR-CCT and RP-CCT inoperable, 6
- 1. Perform a CHANNEL CHECK using local monitor indication within 8 hours9.259259e-5 days <br />0.00222 hours <br />1.322751e-5 weeks <br />3.044e-6 months <br /> and at least once per 8 hours9.259259e-5 days <br />0.00222 hours <br />1.322751e-5 weeks <br />3.044e-6 months <br /> thereafter, and
- 2. Restore the MCR-CCT or RP-CCT to OPERABLE status for the applicable channel (s) within the next 30 days, and if unsuccessful, prepara and submit to the Regional Administrator of the Regional Office of the I NRC within the next 10 days a Special Report outlining the cause of the CCT failure or malfunction and the action taken to restore the inoperable equipment to OPERABLE status.
- b. With the Post-treatment Off-gas PRM High Range ,
Noble Gas Activity Monitor otherwise inoperable, l ctrluent releases via this pathway may continue provided grab samples are taken at least once per 8 hours9.259259e-5 days <br />0.00222 hours <br />1.322751e-5 weeks <br />3.044e-6 months <br /> and analyzed for gross noble gas
- activity within 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br />.
R""?9IAL With the number of channels OPERABIE less than RT ~IREMENT required by the Minimum Channels OPERABLE require-7 ment, effluent releases via this pathway may continue provided the flow rate is estimated at least once per 8 hours9.259259e-5 days <br />0.00222 hours <br />1.322751e-5 weeks <br />3.044e-6 months <br />.
CLINTON-1 3-36 Rev.6-12/89 .
OPPODCM
~
TABLE 3.9.1-2 OFFCAS P%DIATION MONITORING INSTRUMENTATION SURVEILIANCE REOUIREMENTS CHANNEL CHANNEL CHANNEL SOURCE FUNCTIONAL CHANNEL INSTRUMENTATION CHECK CHECK TEST CALIBRATION
- 1. Pre-Treatment Off-gas D(3) M Q(1) R(2)
PRM-Noble Gas Activity Monitor
- 2. Post-Treatment Off-gas PRM
- a. HighRtnge Noble D I3) D Q(1) R(2)O Gas Activity Monitor Providit.g Alarm and Autor::atic Termination of ;
f>elease .
t
- b. EfGteent System D NA Q R i Flow-Rute Measuring l Device .
- c. Sample " low-Rate D NA Q R-Measuring Device l
l l'
CLINT 1 . 3-37 Rev.6-12/89
- - . . ._ --__-- _- .-. . .- . _ . . -- =
- . - - , .~ .
-CPS-ODCM l
TABLE 3.9.1-2 (Continued)
OFFGAS RADIATION MONITORING INSTRUMENTATION SURVEILLANCE REOUTREMENTS TABLE NOTATION
$ Automatic isolation of valve IN66-F060 shall be demonstrated during the CHANNEL CALIBRATION.
(1) The CHANNEL FUNCTIONAL TEST shall also demonstrate that the MCR-CCT or RP-CCT responds with annunciation and event printout to each of the following conditions:
- 1. Instrument indicates measured levels above the alarm / trip (HIGH) setpoint.
- 2. Detector failure (LOW FAIL, HI FAIL) .
- 3. Sample flow failure (EXTERNAL FAIL) .
- 4. Instrument not set in nonal operate mode (UNINITIALIZED, CALIBRATE, MAINTENANCE, or STANDBY).
(2) 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 NIaT.
These standards shall permit calibrating the system over its intended energy range and measurement range. Subsequent CHANNEL CALIBRATION shall be performed using the initial radioactive standards or other standards of equivalent quality or radioactive sources that have been related to the initial calibration.
(3) The CHANNEL CHECK shall also determine that channel '
communication is established to the MCR-CCT or RP-CCT.
t 5
i
_CLINTON-1 3-38 Rev.6-12/89 n- s .e - , <~, -, ,v+- , , , w..-, ,- m --- m an- -~~a - - - --.en,-- --- ,~ --m, , ,,, ,
CPS-ODCH I
3.9.2 Radioactive Gascoun Effluent Monitoring Instrumentation -
Operation and Surveillance Requirements OPERATION REOUTREMENT The radioactiva gaseous effluent monitoring instrumentation channels shown in Table 3.9.2-1 shall be OPERABL2 with their clarm/ trip setpoints set to ensure that the limits of Section 3.4.1 j cnd Technical Specification 3.7.8.2 are not exceeded. The l clarm/ trip setpoints of these channels shall be determined and l cdjusted in accordance with the methodology and parameters in the i this n .ual. This requirement applies as shown in Table 3.9.2-1.
l l
REMEDIAL REOUIREMENT:
I
- a. With a radioactive gaseous effluent monitoring instrumentation channel alarm / trip setpoint less conservative than required by the above requirement, immediately suspend the release of i radioactive gaseous affluents monitored by the affected !
I channel, or declare the channel inoperable.
- b. With less than the minimum number of radioactive gaseous affluent monitoring instrumentation channels OPERABLE, comply i with the REMEDIAL REQUIREMENT specified in Table 3.9.2-1.
Restore the inoperable instrumentation to OPERABLE status within 30 days and, if unsuccessful, explain in the next Semiannual Radioactive Effluent Release Report pursuant to Technical Specification 6.9.1.7 why this inoperability was not corrected in a timely manner.
SURVETLLANCE REOUTREMENTS !
3.9.2.1_ Each radioactive gaseous effluent monitoring instrumentation channel shall be demonstrated OPERABLE by performance of the CHANNEL CHECK, SOURCE CHECK, CHANNEL CALIBRATION and CHANNEL FUNCTIONAL TEST operations at'the frequencies shown in Table 3.9.2-2.
3-39 Rev.6-12/89 CLINTON-1
_ - y . -
.- ~ ~
l -
CPS-OD-Q V. ,
.- I TABLE 3.9.2-1 I RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION MINIMUM g REMEDIAL IljSTRUMENT CHANNEIS OPERABLE APPLICABILITY REOUIREME*4T
- a. liigh-Range Noble. Gas 1(a) , g Activity Monitor.
- b. Low-Range Noble Gas -
1(a) '* 8 Activity Monitor i t
l c. Iodine Sampler (1). 1 ,
9 l d. Particulate SamplerI1)' .
- 9 l! e. Sample Flow-Rate 1
- 10 ,
1 Measuring Device *
- f. Effluent System Flow 1
- 10 '
Rate Measuring Device I
. Exhaust PRM
' I
- a. High-Range Noble Gas 1(a) ** 8 L D-[- 87-c2_
Activity Monitor
- b. Low-Range Noble Gas 1(a) ** 8 i Activity Monitor -
i .
i i
- i. .
}
i
. t CLINTON-1 3-40 I Rev.8-7/91 '
CPS-OC N -N TABLE 3.9.2-1 (Continued) .*
RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION MIN 7 MUM g REMEDIAL INSTRUMENT CHANNELS OPERABLE APPLICf.BILTTY REOUIREMENT
- 2. Standby Gas Treatment System Exhaust PRM (Continued)
- c. Iodine Sampler (1) 1 ** 9 L
{' d. Particulate Sampler (1) y ,, 9
- e. Sample Flow-Rate 1 ** 10 Measuring Device
- f. Effluent System Flow- 1 ** 10 c Cs Rate Measuring Device 0 ;]4j :
7
. ie d
. CLIN 1 ,1 3-41 gey,g_7/91
CPS-ODCM TABI E 3.9.2-1 (Continuedl RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION TABLE NOTATIONS
- At all times.
- During standby gas treatment system operati,
- A channel may be placed in an inoperable status for up to 1 hour1.157407e-5 days <br />2.777778e-4 hours <br />1.653439e-6 weeks <br />3.805e-7 months <br /> for the purpose of performing surveillances.
(a) Channel OPERABILITY shall include the capability of either the Main Control Room Central Control Terminal (MCR-CCT) or the Radiation Protection Office Central Control Terminal (RP-CCT) to provide the alarm status of the applicable radiation monitor channel (s).
(1) Filter media (particulate collection patch for particulates and charcoal cartridge for iodines) in place with an operating sample pump constitutes an iodine / particulate sampler.
9 REMEDIAL REOUIREMENT REMEDIAL a. With both the MCR-CCT and RP-CCT inoperable, KEQUIREMENT perform a CHANNEL CHECK using local monitor 8 indication within 8 hours9.259259e-5 days <br />0.00222 hours <br />1.322751e-5 weeks <br />3.044e-6 months <br /> and at least once per 8 hours9.259259e-5 days <br />0.00222 hours <br />1.322751e-5 weeks <br />3.044e-6 months <br /> thereafter.
- b. With the noble gas activity monitor channel (s) otherwise inoperable, effluent releases via this pathway may continue provided grab samples are taken at least once -
per 8 hours9.259259e-5 days <br />0.00222 hours <br />1.322751e-5 weeks <br />3.044e-6 months <br /> and analyzed for gross noble gas activity within 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br />.
REMEDIAL With the number of channels OPERABLE less than REQUIREMENT required by the Minimum Channels OPERABLE
- 9 requirement, effluent releases via this pathway may continue provided that, within 4 hours4.62963e-5 days <br />0.00111 hours <br />6.613757e-6 weeks <br />1.522e-6 months <br /> after the channel has been declared inoperable, samples required by Table 3.4-1 are continuously collected with auxiliary sampling equipment.
s REMEDIAL With the number of channels OPERABLE less than REQUIREMENT required by the Minimum Channels OPERABLE 10 requirement, effluent releases via this pathway may continue provided the flow rate is estimated at least once per 4 hours4.62963e-5 days <br />0.00111 hours <br />6.613757e-6 weeks <br />1.522e-6 months <br />.
CLINTON-1 3-42 Rev.8-7/91
CPS-ODCM TABLE 3.9.2-2 a
- RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION SURVEILLANCE REOUIREMENTS' CHANNEL CHANNEL . SOURCE CHANNEL FUNCTIONAL INSTRUMENT CHECK CHEC_E CALIBRATION TEST APPLICABILITY
- a. High-Range Noble' D I3) M R(2) Q(4 '
Gas Activity Monitor
- b. Low-Range Noble D(3) M R(2) Q(1)
Gas Activity Monitor W NA NA NA *
- c. Iodine Sampler .
W NA NA NA
- d.. Particulate Sampler ,
D NA R Q *
- e. Sample Flow Rate Measuring Device D NA R Q *
- f. Effluent System Flow Rate Measuring Device
- 2. Standby Gas Treatment System Exhaust PRM D(3) Q(1) **
- a. High-Range Noble NA R(2)
Gas Activity Monitor
- b. Low-Range Noble D(3) M R(2) Q(1) **
Gas Activity. Monitor CLIr 11 - 1 3-43 Rev.6-12/
CPS-ODL.. v TABLE 3.9.2-2 (Continued) j l
RADIOACTIVE GASEOUS EFFUIENT MONITORING INSTRUMENTATION SURVEILLANCE REOUIREMENTS l l
CIIANNEL CIIANNEL SOURCE CHANNEL FUNCTIONAL INSTRUMENT CilECK CllECK CALTBRATION TEST APPLTCABILITY l
- c. Iodine Sampler W NA NA NA l I
NA NA **
- d. Particulate W NA l Sampler D NA R Q **
- e. Sample Flow-Rate Measuring Device Effluent' System D NA R Q **
f.
Flow-Rate Measuring Device CLINTON-1 3-44 Rev.6-12/89 i _ _ _ _ _ . . . .
TABLE 3.9.2-2 (Continued)
EADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION SURVEILLANCE REOUIREMENTS TABLE NOTATIONS
- At all times.
- During operation of the standby gas treatment system.
(1) The CHANNEL FUNCTIONAL TEST shall also demonstrate that the MCR-CCT or Rp-CCT responds with annunciation and event printout to each of the following conditions:
- 1. Instrument indicates measured levels above the alarm u (HIGrf) setpoint,
- 2. Detector failure (LOW FAIL, HI FAIL) .
- 3. Sample flow failure (EXTERNAL FAIL)
R 4. Instrument not set in normal operate mode (UNINITIALIZED, CALIBRATE, MAINTENANCE, or STANDBY).
(2) 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.
These standards shall permit calibrating the system over its Subsequent intended range of energy and measurement range.
CHANNEL CALIBRATION shall be performed using the initial radioactive standards or other standards of equivalent quality or radioactive sources that have been related to the initial ,
calibration.
(3) The CHANNEL CHECK snall also determine that channel communication is established to the MCR-CCT or RP-CCT.
3-45 Rev.6-12/89 CLINTON-1
j J , . ,.' ,
v
~
4 Fiqure 3.1-1
. 2
[ .
i ,. -
1z CPS- SITE BOUNDARY'FOR GASEOUS EFFLUENTS 8 i
.o H- 3 N
t k
/
fjf, . i "as"oun'I;*t EcA' j
LEGEND m - / -
StrE BOutOARY i
- y 7j e uNRESnuerEo AREA M
,s.. EN.S"t otEt) :
) ( , .
ancocoow) " 7008ANNEErwNEo BYIPC.-
['] f "" ( usanaea yw '
- , " Ag/////r///n%7/P " " "
wes i
/
b ', lf' , L NOTES
' / 1. THE AREA IN THE 1)XE BETWEEN THE BUOYS
/ . AND THE SECLUSION AREA BOUNDARY IS j/' .
,, , UNRESTRICTED AT THIS TiuE. BUT W1.L BE
/ CCNTROLLED !F PLANT EFFLUENT cot 0!TIONS
- g g , ,
WARRANT CLOSURE.
- <- j_ wt smnce (et s) 2. LAND PARCEL NOT OWNED BY E.LINOIS POWER.
'm ,
INQ.UDES RESIDENCES.
b 3. LAND PARCEL F40T OWNED BY LLINOIS POWER, g ,g OL CouPAff( PIPELINE PUUPING STATION. '
1 P Ncnt 4 4. LAND PARCEL NOT OWNED BY titNOIS POWER -
AGRICULTURAL USE. ,
- 5. THE LAKE SHORELINE IS APPROX!MATELY 690 FT.
USL ELEVATION LINE.
.. . _ ~ . - . . . ~ .. -. --_, . ~ . . ~ - . . .. .
I ODCM FIGURE 3.3-1 MAIN CONDENSER OFF-GAS-' TREATMENT SYSTEM ,
a
- M38 *cPtEE. Pet 001
,manunA
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(] 1CD01A aatts-evioo.
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PRIMARY / SECONDARY l cnNTAfNtFNT EXHAUST l
- Monitors required by Sections 3.9.1 and 3.9.2 1CD01A Main OCA0lTA CV 1N66B010B Cooler 1N66D013 1RIX-PR035 0.ff-Cas Condanser Separator Tank'A Condenser B Charcoal Adsorber Post Treatment PRM 1CA01AA Steam Jet OCA01TB CV 1N66Z003A IN66D01o HEPA 1RIX-PR041 Off-Cas Air Ejector A Separator Tank B Dessicant Dryer A Filter Post Treatment PRM 1CA01AB Steam Jet 1N66D005A IN66 ZOO 3B ORIX PR001 HVAC ORIX-PR003 Standby Air Ejector B Recombiner A Dessicant Dryer B Stack PRM #1 Cas Treatment PRM OCA01PA Condenser 1N66D005B 1N66B011 Gas ORIX-PR002 HVAC ORIX-PR004 Standby Vacuum (CV) Pump A Recombiner B Cooler Stack PRM #2 Cas Treatment PPJi OCA0lPB CV Pump B 1N66B010A Cooler IN66D012 1RIX-PR034 Off-Cas Condenser A Charcoal Adsorber Pretreatment PRM
. .l
'CLINTON-1 3-47 Rev.8-7/91 y e,
CPS 0DCM Table 3.5-1 INHALATION DOSE FACTORS FOR INFANT - (DFA1)a (mrem per pci inhaled)
NUCLIDE BONE LIVER T. BODY THYROID KTDNEY LUNG GI-LLI
-H-3 NO DATA 4.62E 07 4.62E 07 4.62E-07 4.62E 07 4.62E-07 4.62E-07 C-14 1.89E-05* 3.79E 06 3.79E 06 3.79E-06 3.79E 06 3.79E 06 3.79E 06 NA-24 7.54E-06 7.54E 06 7.54E 06 7.54E 06 7.54E 06 7.54E 06 7.54E 06 P 32 1.45E-03 8.03E 05 5.53E-05 NO DATA NO DATA NO DATA 1.15E 05 CR-51 NO DATA NO DATA 6.39E 08 4.11E 08 9.45E-09 9.17E-06 2.55E-07 MN 54 NO DATA 1.81E-05 3.56E 06 NO DATA 3.56E-06 7.14E-04 5.04E-06 MN-56 NO DATA 1.10E-09 1.58E-10 NO DATA 7.86E-10 8.95E-06 5.12E 05 FE 1.41E-05 8,39E 06 2.38E 06 NO DATA NO DATA 6.21E 05 7.82E 07 FE-59 9.69E 06 1.68E-05 6.77E-06 NO DATA NO DATA 7.25E-04 1.77E.05 CO-58 NO DATA '8.71E 07 1.30E 06 NO DATA NO DATA 5.55E 04 7.95E-06 CO-60 NO DATA 5.73E-06 8.41E 06 NO DATA NO DATA 3.22E-03 2.28E-05 2.42E-04 1.46E-05 8.29E-06 NO DATA NO DATA 1.49E 04 1.73E 06
) NI-63 NI 65 -1.71E-09 2.03E-10 8.79E 11 NO DATA NO DATA 5.80E-06 3.58E 05 CU-64 NO DATA 1.34E 09 5.53E-10 NO DATA 2.84E-09 6.64E-06 1.07E 05 ZN-65 1.38E-05' 4.47E-05 2.22E-05 NO DATA 2.32E-05 4.62E-04 3.67E 05 ZN-69 3.85E-11 6.91E-11 5.13E-12 NO DATA 2.87E 11 1.05E-06 9.44E 06 BR-83 NO DATA NO DATA 2.72E-07 NO DATA NO DATA NO DATA LT E-24**
BR-84 NO DATA NO DATA 2.86E-07 NO DATA. NO DATA NO DATA- LT E 24 BR-85 'NO DATA NO DATA 1,46E-08 NO DATA NO DATA NO DATA LT E-24 RB-86 -NO DATA 1.36E-04 6.30E-05 NO DATA NO DATA NO DATA 2.17E-06 RB-88 NO DATA- 3.98E-07 2.05E-07 NO DATA NO DATA NO DATA 2.42E-07 RB NO DATA 2.29E-07 1.47E 07- NO DATA NO DATA NO DATA 4.87E 08 SR-89 2.84E-04 NO DATA 8.15E 06 NO DATA NO DATA 1.45E-03 4.57E-05
'SR 90 2.92E-02 NO DATA 1 85E-03 NO DATA NO DATA 8.03E 03 9.36E-05 SR-91 6.83E NO DATA 2.47; ')9 NO DATA NO DATA 3.76E-05 5.24E-05 SR-92 7.50E-09 NO DATA 2.79E-10 NO DATA NO DATA 1.70E-05 1.00E 04 Y-90 2.35E-06 NO DATA 6.30E-08 NO DATA NO DATA 1.92E-04 7.43E-05 l
CLINTON-1 3-48 Rev.5-2/89
. , , - . .- - .. _ _ . ~ ~ . - - . .- . ~ . - - .-
CPS-ODCM:
Table 3.5-1 (continued) ,
i
~ INHALATION DOSE FACTORS FOR INFANT - (DFAi)a i (mrem per pCi inhaled)
BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI NUCLIDE Y 91m 2.91E-10 NO DATA 9.90E-12 NO DATA NO DATA 1.99E 06 1.68E 06 Y-91 4.20E 04 NO DATA 1.12E 05 NO DATA NO DATA 1.75E 03 5.02E-05 1.17E 08 -NO DATA 3.29E 10 NO DATA NO DATA 1.75E-05 9.04E 05 Y 92 Y-93 1.07E-07 NO DATA 2.91E 09 NO DATA NO DATA 5.46E 05 1.19E 04 ZR-95 8.24E-05 1.99E 1.45E 05 NO DATA 2.22E 05 1.25E-03 1.55E 05 1.07E-07 1.83E-08 8.36E-09 NO DATA 1.85E-08 7.88E-05 1.00E 04 ZR-97 NB 1.12E-05 4.59E 06 2.70E-06 NO DATA 3.37E 06 3.42E-04 9.05E-06 MO 99 NO DATA 1.18E-07 2.31E 08 NO DATA 1.89E 07 9.63E 05 3.48E-05 TC-99m 9.98E-13 2.06E-12 2.66E-11 NO DATA 2.22E-11 5.79E-07 1.45E 06 4.65E-14 5.88E-14 5.80E-13 NO DATA 6.99E-13 4.17E-07 6.03E 07 TC 101 RU 103 1.44E-06 NO DATA 4.85E-07 NO DATA 3.03E-06 3.94E-04 1.15E-05
-RU-105 8.74E 10 NO DATA 2.93E 10 NO DATA 6.42E-10 1.12E-05 3.46E 05 g~
'6.20E 05 NO DATA 7.77E 06 NO DATA 7.61E-05 8.26E 03 1.17E 04 RU-106-7.13E 06 5.16E-06 3.57E-06 NO DATA 7.80E-06 2.62E-03 2.36E-05 AG 110m
-3.40E-06 4.70E 07 1.16E 06 NO DATA 3.19E 04 9.22E 06 TE-125m .
_1.42E-06 1.19E-05 4.93E-06 1.48E 06 3.48E 06 2.68E 05 9.37E 04 1.95E-05 TE-127m 1.59E-09 6.81E-10 3.49E 10 1.32E-09 3.47E 09 7.39E-06 1.74E-05 TE-127 1.01E-05 4.35E-06 1.59E-06 3.91E 06 2.27E 05 1.20E-03 4.93E 05 TE-129m 5.63E-11 2.48E-11 1.34E-11 4.82E-11 1.25E-10 2.14E 06 1.88E 05 TE 129 7.62E-08 3.93E-08 2.59E-08 6.38E 08 1.89E 07 1.42E-04. 8.51E 05 TE-131m 1.24E-11 5.87E-12 3.57E-12 1.13E-11 2.85E-11 1.47E-06 5.87E-06 TE-131 -
2.66E 07 1.69E-07 1.26E 07 1.99E-07 7.39E-07 2.43E-04 3.15E 05 TE-132 9.91E-06 3.98E-06 1.14E-03 1.09E-05 NO DATA 1.42E-06 I-130 4'.54E-06 7.56E-07 2- I 131' 2.71E-05 3.17E-05 1.40E-05 1.06E-02 3.70E 05 NO DATA s
2.53E 8.99E-07 1.21E-04 2.82E-06 NO DATA 1.36E-06 1-132 1.21E-06 1.37E-05 4.00E 06 2.54E-03 1.60E-05 NO DATA 1.54E-06 1-133 9.46E-06 6.58E 07 1.34E-06 4.75E-07 3.18E-05 1.49E-06 NO DATA 9.21E-07 I-134 l.
l l
CLINTON-1 3-49 Rev 5-2/89
CPS-ODCM Table 3.5-1 (continued)
INHALATION DOSE FACTORS FOR INFANT - (DFA1)a (mrom per pCi inhaled)
NUCLIDE BONE LIVER T. BODY THYPOID KIDNEY LUNG CI-LLI I-135 2.76E 06 5.43E 06 1.98E 06 4.97E-04 6.05E 06 NO DATA 1.31E-06 CS 134 2.83E 04 5.02E 04 5.32E-05 NO DATA 1.36E-04 5.69E-05 9.53E-07 CS-136 3.45E 05 9.61E 05 3,78E 05 NO DATA 4.03E-05 8.40E 06 1.02E-06 CS-137 3.92E 04 4.37E-04 3.25E-05 NO DATA 1.23E-04 5.09E-05 9.53E 07 CS 138 3.61E 07 5.58E-07 2.84E 07 NO DATA 2.93E-07 4.67E 08 6.26F 07 BA-139 1.06E 09 7.03E-13 3.07E-11 NO DATA 4.23E-13 4.25E 06 3.64E 05 BA-140 4.00E 05 4.00E-08 2.07E-06 NO DATA 9.59E-09 1.14E-03 2.74E 05 BA-141 1.12E 10 7.70E-14 3.55E-12 NO DATA 4.64E 14 2.12E-06 3.39E 06 BA-142 2.84E-11 2.36E 14 1.40E-12 NO DATA 1.36E-14 1.11E 06 4.95E 07 LA-140 3.61E 07 1.43E-07 3.68E-08 NO DATA NO DATA 1.20E 04 6.06E-05 LA-142 7.36E-10 2.69E-10 6.46E-11 NO DATA NO DATA 5.87E 06 4.25E 05 1.98E-05 1.19E 05 1.42E-06 NO DATA 3.75E 06 3.69E-04 1.54E 05
) CE-141 CE-143 2.09E-07 1.38E-07 1.58E-08 NO DATA 4.03E-08 8.30E 05 3.55E-05 CE 144 2.28E 03 8.65E-04 1.26E-04 NO DATA 3.84E-04 7.03E-03 1.06E-04 PR-143 1.00E 05 3.74E-06 4.99E-07 NO DATA 1.41E-06 3.09E 04 2.66E-05 PR-144 3.42E-11 1.32E-11 1.72E-12 NO DATA 4.80E-12 1.15E.06 3.06E-06 ND-147 5.67E-06 5.81E-06 3.57E-07 NO DATA 2.25E-06 2.30E-04 2.23E.05 W-187 9.26E 09 6.44E 09 2.23E-09 NO DATA NO DATA 2.83E-05 2.54E-05 NP-239 2.65E-07 2.37E-08 1.34E-08 NO DATA 4.73E-08 4.25E-05 1.78E-05
- 1.89 X 10-05
- Less than 10-24 CLINTON-1 3-50 Rev.5-2/89
, CN-6DCM i
Table 3.5-1 ,
I INHALATION DOSE FACTORS FOR CHILD - (DFA1)a (mrem per pCi inhaled)
LIVER T. BODY "'HYROID KIDNEY LUNG GI-LLI NUCLIDE BONE 3.04E-07 3.04E 07 3.04E-07 3.04E 07 3,04E 07 H3 NO DATA 3.04E 07 C-14 9.70E 06* 1.82E-06 1.82E 06 1.82E 06 -1.82E 06 1.82E 06 1~82E-06 NA 24 4.35E-06 4.35E 4.35E-06 4.35E-06 4.35E 06 4.35E 06 4.35E 06 2.67E 05 NO DATA NO DATA NO DATA - 1,14E-05 P 32 7.04E 04 3.09E-05
-CR-51 NO DATA NO DATA 4.17E 08 2.31E-08 6.57E-09 4.59E-06 2.93E-07 MN 54 NO DATA 1.16E-05 2.57E 06 NO DATA 2.71E-06 4.26E-04 6.19E-06 MN 56 NO DATA 4.48E-10 8.43E-11 NO DATA 4.52E-10 3.55E-06 .3.33E-05 FE 55 1.28E-05 6.80E-06 2.10E-06 NO DATA NO DATA 3.00E 05 7.75E-07 FE 59 - 5.59E-06 9.04E-06 4.51E 06 NO DATA NO DATA 3.43E-04 1.91E-05 CO-58 NO DATA 4.79E-07 8.55E 07 NO DATA NO DATA 2.99E-04 9.29E-06 6.12E-06 NO DATA 1.91E 03 2,60E 05
-CO 60- NO DATA- 3.55E 06 NO DATA NI 63 -2.22E-04 1.25E-05 7.56E-06 NO DATA NO DATA 7.43E-05 1.71E-06
-)
NI-65 8.08E-10 7.99E 11. 4.44E 11 NO DATA NO DATA 2.21E-06 2.27E-05 CU-64 NO DATA 5.39E-10 2.90E-10 NO DATA 1.63E 09 2.59E 06 9.92E 06 ZN 1.15E 05 3.06E-05 1.90E-05 NO DATA 1.93E 05 2.69E 04 4.41E-06 ZN-69 1.81E-11 -2,61E 11 2.41E-12 NO DATA 1.58E-11 3.84E-07 2.75E 06 BR 83 NO DATA NO DATA 1.28E-07 NO DATA NO DATA NO DATA LT E 24**
BR-84 . NO DATA- -NO DATA 1.48E-07 NO DATA NO DATA NO DATA LT E 24 BR-85 ;NO DATA 6.84E 09 NO DATA NO DATA NO DATA LT E-24 NO DATA _
RB-86 NO DATA 5.36E-05 3.09E-05 NO DATA 'NO DATA NO DATA 2.16E-06 RB-88 NO DATA 1.52E-07 9.90E-08 NO DATA NO DATA NO DATA 4.66E 09
- RS NO DATA 9.33E-08 7.83E 08 NO DATA NO DATA NO DATA 5.11E 10 SR-89 1.62E-04 NO DATA 4.66E 06 NO DATA NO DATA 5.83E 04 4.52E 05 SR-90 2.73E-02 NO DATA 1.74E-03 NO DATA NO DATA 3.99E 03 9.28E 05 CLINTON-1 3-51 Rev.5-2/89
~ v . - - . ~ ,,
- . -- .- - - - - . . _. -. . ~ . - . - . . - - . . ~ . . -
CPS-ODCM Table 3.5-2 (continued)
INHALATION DOSE FACTORS FOR CHILD - (DFA1)a (mrem per pCi inhaled)
NUCLIDE BONE LIVER T. BODY E '3OID KIDNEY LUNG -GI-LLI SR-91 3.28E-08 NO DATA 1.24E-09 NO DATA NO DATA 1.44E-05 4.70E 05 SR 92 3.54E 09 NO DATA 1.42E 10 NO DATA NO DATA 6.49E-06 6.55E 05 Y 90 1.11E-06 NO DATA 2.99E 08 NO DATA NO DATA 7.07E 05 7.24E 05 Y-91m 1.37E-10 NO DATA 4.98E 12 NO DATA NO DATA 7.60E 07 4.64E 07 Y-91 2.47E-04 NO DATA 6.59E-06 NO DATA NO DATA 7.10E-04 4.97E-05 Y 92 5.50E-09 NO DATA 1.57E-10 NO DATA NO DATA 6.46E 06 6.46E 05 Y-93 5.04E-08 NO DATA 1.38E-09 NO Di"A NO DATA 2.01E 05. 1.05E 04 ZR-95 5.13E 05 1.13E 05 1.00E 05 NO DATA 1.61E 05 6.03E 04 1.65E-05 ZR 97 5.07E 08 7.34E 09 4.32E-09 NO DATA 1.05E 08 3.06E 05 9.49E 05 NB-95 6.35E-06 2.48E 06 1.77E 06 NO DATA 2.33E-06 1.66E 04 1.00E 05 MO-99 110 DATA 4,66E-08 1.15E-08 NO DATA 1.06E-07 3.66E 05 3.42E-05
.TC 99m ,4.81E-13 _9.41E 13 1.56E 11 NO DATA 1.37E 11 2.57E 07 1.30E 06
)
TC-101 2.136-14 2.30E-14 2.91E 13 NO DATA 3.92E-13 1.58E 07 4.41E-09 RU-103 7.55E-07 NO. DATA 2.90E 07 NO DATA 1.90E 06 1.79E 04 1.21E 05 RU 105- 4.13E 10- NO DATA 1.50E 10 NO DATA 3.63E 10 4.30E-06 2.69E 05 RU 106 3.68E-05 NO DATA 4.57E-06 NO DATA 4.97E-05 3.87E-03 1.16E-04 AC-110m 4.56E-06 3.08E-06 2.47E-06 NO DATA 5.74E-06 1.48E-03 2.71E-05 TE 125m 1.82E-06 6.29E 07- 2.47E-07 5.20E,07 NO DATA 1.29E-04 9.13E 06 TE-127m 6.72E-06_ 2.31E-06 8.18E-07 1.64E-06 1.72E-05 4.00E 04 1.93E-05 TE-127 7.49E-10 '2.57E-10 1.65E-10 5.30E-10 1.91E-09 2.71E-06 1.52E 05 TE-129m 5.19E-06 1.85E-06 8.22E-07 1.71E-06 1.36E-05 4.76E-04 4. 91E 05 TE 129 2.64E-11 9.45E-12 6.44E-12 1.93E-11 6.94E-ll 7.93E 07 6.89E 06 TE 131m 3.63E-08 .1.60E 08 1.37E 08 2.64E-08 1.08E-07 5.56E-05 8.32E 05 TE-131 5.87E-12 2.28E-12 1.78E 12 4.59E-12 1.59E-11 5.55E 07 3.60E 07 TE-132 1.30E-07. 7.36E 08 7.12E 08 8.58E 08 4.79E-07 1.02E-04 3.72E 05 I-130 2.21E-06 4.43E-06 2.28E 06 4.99E-04 6,61E-06 NO DATA 1.38E 06 I-131 1.30E-05 1.30E-05 7.37E-06 4.39E-03 2.13E-05 NO DATA 7.68E 07 CLINTON-1 3-52 Rev 1-11/85
.~,
~ .- .- . - - -. - - . ..
CPS-ODCM Table 3.5-2 (continued)
INHALATION DOSE FACTORS FOR CHILD - (DFAi)a (mrom per pCi inhaled)
LIVER T. BODY THYROID KIDNEY LUNG GI-LLI NUCLIDE BONE 2 132 5.72E-07 1.10E 06 5.07E 07 5.23E-05 1.69E 06 NO DATA 8.65E 07
.3-133 4.48E 06 5.49E-06 2.08E 06 1.04E 03 9.13E 06 NO DATA 1.48E 06 2-134 3.17E-07 5.84E-07 -2.69E 07 1.37E 05 8.92E 07 NO DATA 2.58E 07 1 135 1.33E-06 2.36E 06 1.12E-06 2.14E-04 3.62E-06 NO DATA 1.20E 06 CS-134 1.76E-04 2.74E-04 6.07E 05 NO DATA 8.93E 05 3.27E-05 1.04E-06 CS-136 1.76E-05 4.o2E 05 3.14E-05 NO DATA 2.58E-05 3.93E-06 1.13E 06 C3-137 2.45E 04 2.23E-0A 3.47E-05 NO DATA 7.63E-05 2.81E-05 9.78E 07 CS-138 1.71E-07 2.27E-07 1.50E 07 NO DATA 1.68E-07 1.84E 08 7.29E 08 BA-139 4.98E 10 2.66E-13 1.45E-11 NO DATA 2.33E-13 1.56E-06 1.56E 05 BA-140 2.00E-05 1.75E-08 1.17E 06 NO DATA 5.71E 09 4.71E-04 2.75E-05 BA-141 5.29E-11 2.95E-14 1,72E-12 NO DATA 2.56E-14 7.89E-07 7.44E-08 BA-142 1.35E-11 9.73E-15 -7.54E-13 NO DATA 7.87E-15 4.44E-07 7.41E-10 LA-140 1.74E-07 6.08E-08 2.04E 08 NO DATA NO DATA 4.94E 05 6.10E 05 3.50E-10 1.11E-10 3.49E-11 NO DATA NO DATA 2.35E 06 2.05E-05 M-142 1.53E-05 CE-141 1.06E-05. -5.28E 06 7.83E-07 NO DATA 2.31E-06 1.47E-04 CE-143 9.89E-08 5.37E-08 7.77E 09 NO DATA 2.26E-08 3.12E 05 3.44E 05 CE 144 1.83E-03 5.72E-04 9.77E 05 NO DATA 3.17E-04 3.23E 03 1.05E-04 4.99E 06 1.50E-06 2.'47E-07 NO DATA 8.11E-07 1.17E-04 2.63E-05 PR-143 4.99E-12 8.10E-13 NO DATA 2.64E-12 4.23E-w 5.32E-08 i PR-144' l.61E-11 2.92E-06 2.36E-06 1.84E-07 NO DATA 1.30E-06 8.87E 05 2.22E 05 ND-147
.W-187 4.41E 09 2.61E-09 1.17E 09 NO DATA NO DATA 1.11E 05 2.46E-05 1.26E-07 9.04E-09 6.35E 09 NO DATA 2.63E-08 1.57E 05 1.73E 05 NP 239
.
- 9.70 X-10 -06 I
- Less than 10-24 CLINTON-1 3-53 Rev.1-11/85
.. . . - . . . . . . -. .- - .- ~_ .- ~ ~ . _ . . - . --
CPS-ODCM Table 3.5-3 INHALATION DOSE FACTORS FOR TEEN - (DFA1)a (mrem per pCi inhaled)
-NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI
.H3 NO DATA 1.59E 07 1.59E-07 1.59E-07 1.59E-07 1.59E-07 1.59E-07 C 14 3.25E 06* 6.09E-07 6.09E 07 6.09E 07 6.09E-07 6.09E-07 6.09E 07 NA-24 1.72E-06 1.72E 06 1.72E-06 1.72E 06 1.72E 06 1.72E 06 1.72E 06 P 32 2.36E 04 1.37E-05 8.95E-06 NO DATA NO DATA NO DATA 1.16E 05 CR 51 NO DATA NO DATA 1.69E 08 9.37E 09 3.84E 09 2.62E-06 3.75E 07 MN-54 NO DATA 6.39E-06 1.05E-06 NO DATA 1.59E 06 2.48E 04 8.35E 06 MN 56 NO DATA 2.12E 10 3.15E-11 NO DATA 2.24E-10 1.90E 06 7.18E-06 FE-55 4.18E-06 2.98E 06 6.93E-07 NO DATA NO DATA 1.55E-05 7.99E 07 FE 59 1.99E-06 4.62E 06 1.79E 06 NO DATA NO DATA 1.91E-04 2.23E 05 CO-58 NO. DATA 2.59E 07 3.47E-07 NO DATA NO DATA 1.68E 04 1.19E-05 CO 60 NO DATA 1.89E 06 2.48E 06 NO DATA NO DATA 1.09E-03 3.24E 05 NI-63 - 7.25E 05 5.43E-06 2.47E 06 NO DATA .NO DATA 3.84E-05 1.77E 06
)
NI-65 2.73E-10 3.66E 11 1.59E-11 NO DATA NO DATA 1.17E-06 4.59E 06 CU NO DATA 2.54E-10 1.06E-10. NO DATA 8.01E-10 1.39E-06 7.68E 06 ZN-65 - 4.82E-06 1.67E-05 7.80E-06 NO DATA 1.08E-05 1.55E 04 5.83E 06 ZN-69 6.04E-12 1.15E 11 8.07E-13 NO DATA 7.53E-12 1.98E-07 3.56E 08 BR-83 NO DATA NO DATA 4.30E-08 NO DATA NO DATA' NO DATA LT E-24**
BR 84 NO DATA 'NO DATA 5.'41E- 08 NO DATA
- NO DATA NO DATA LT E 24 BR-85 NO DATA NO DATA 2.29E 09 NO DATA NO DATA NO DATA LT E 24 RB-86 NO DATA 2.38E 05 1.05E-05 NO DATA NO DATA NO DATA 2.21E 06 RB 88- NO DATA 6.82E-08 3.40E-08 NO DATA NO DATA NO DATA 3.65E-15 ,
RB-89 NO DATA 4.40E-08 2.91E-08 NO DATA -NO DATA NO DATA 4.22E 17
~ sri 89 - 5.43E-05 NO DATA 1.56E-06 NO DATA NO DATA 3.02E-04 4.64E-05 SR 1.35E 02 NO DATA 8.35E-04 NO DATA NO DATA 2.06E 03 9.56E-05
)
CLINTON-1 3-54 Rev.1-11/85
<-m.e, a v - + ,- -. . - , -+- ,,
s
. . _ _ _ _ . _ ._ m . . . . _ . _- . _ . - __ _ . _ . _ _ _ . _ _ . . - . _ . _ . . .. .
Table 3.5-3 (continued)
INHALATION DOSE: FACTORS FOR TEEN - (DFA1)a (mrem per pCi inhaled)
THYROID KIDNEY LUNG GI LLI yUCLIDE BONE LIVER T. BODY 4.39E-10 NO DATA NO DATA 7.59E 06 3.24E 05
-SR 91 1.10E 08 - NO DATA 5.08E-11 NO DATA NO DATA 3.43E 06 1.49E 05 SR-92 1.19E 09 NO DATA 3.66E-05 6.99E 05 1.00E.08 NO DATA NO DATA
-Y-90 3.73E-07 NO DATA 1.77E 12 NO DATA NO DATA 4.00E-07 3.77E 09 Y 91m 4.63E 11 NO DATA 5.11E-05 2.21E-06 NO DATA NO DATA 3.67E-04 Y-91 8.26E 05 NO DATA 3.35E 06 2.06E-05 1.84E 09 NO DATA 5.36E-11 NO DATA NO DATA Y-92 NO DATA 4.65E 10 NO DATA NO DATA- 1.04E-05 7.24E 05
-Y 93 1.69E-08 3.36E 04 1.86E 05 ZR-95 1.82E-05 3.73E 06 3.94E-06 NO DATA 8.42E 06 1.57E-09 NO DATA 5.15E-09 1.62E 05 7.88E 05 ZR 97 1.72E 08 3.40E-09 7.08E-07 NO DATA 1.25E-06 9.39E 05 1.21E 05 NB-95 2.32E 06 1.29E-06 3.36E-05 2.11E 08 4.03E-09 NO DATA 5.14E-08 1.92E 05 MO-99 NO DATA 7,66E-07 4,83E-13 6.24E-12 NO DATA 7.20E-12 1.44E-07 TC 99m 1.73E-13 1.03E-13 NO DATA 1.90E-13 8.34E-08 1.09E-16 j TC-101 7.40E-15 1.05E-14 1.36E-05 1.12E-07 NO DATA 9.29E-07 9.79E 05 RU 103 2.63E 07 NO DATA 2.27E-06 1.13E 05 RU-105 1.40E 10 NO DATA 5.42E-11 NO DATA 1.76E-10 1.55E-06 NO DATA 2.38E 05 2.01E-03 1.20E 04 RU-106 1.23E 05 NO DATA 8.44E 04 3.41E-05 1 73E-06 1.64E-06 9.99E-07 NO DATA 3.13E-06 AG1-10m 6.70E 05 9.38E 06 TE 125m- 6.10E-07 2.80E 07 8.34E-08 ,
1.75E-0T NO DATA 2.73E-07 -5.48E-07 8.17E-06 2.07E-04 -1.99E 05 TE-127m 2.25E-06 1.02E-06 1,40E 06 1.01E-05 2.51E-10 1.14E-10 5.52E-11 1.77E-10 9.10E-10 TE 127 2.47E 04 5.06E-05 1.74E 06 8.23E-07 2.81E-07 5.72E-07 6.49E 06 TE-129m 6.48E-12 3.32E-11 4.12E-07 2.02E-07 TE-129 8.87E-12 4.22E-12 2.20E-12
- 9.06E-09 5.49E-08 2.97E 05 7.76E-05 TE-131m 1.23E 08- 7.51E-09 5.03E-09 1.55E-12 7.72E-12 2.92E-07 1.89E-09
-TE-131 1.97E-12 1.04E-12 6.30E-13 3-55 Rev.5-2/89 CLINTON-1 l
CPS-ODCM y Table 3.~5-3 (continued)
INHALATION DOSE FACTORS FOR TEEN - (DFA1)a (mrem por pCi inhaled)
NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG CI-LLI TE-132 4.50E 3.63E 08 2.74E-08 3.07E 08 2.'44 E- 07 5.61E 05 5.79E 05 I-130 7.80E-07 2.24E-06 8.96E-07 1.86E-04 3.44E 06 NO DATA 1.14E-06 I-131 4.43E 06 6.14E-06 3.30E 06 1.83E 03 1.05E-05 NO DATA 8.11E 07 I-132 1.99E-07 5.47E-07 1.97E-07 1.89E 05 8.65E-07 NO DATA 1.59E-07 1-133 1.52E 06 2.56E-06 7.78E-07 3.65E-04 4.49E-06 NO DATA 1.29E 06 I-134 1.11E-07 2.90E-07 1.05E-07 4.94E-06 4.58E-07 NO DATA 2.55E-09 Z-135 4.62E-07 1.18E 06 4.36E 07 7.76E-05 1.86E-06 NO DATA 8.69E 07
.CS-134 6.25E-05 1.41E 04 6.86E 05 NO DATA 4.69E-05 1.83E-05 1.22E-06 CS 136 6.44E-06 2.42E-05 1.71E-05 NO DATA 1.38E-05 2.22E 06 1.36E-06 CS-137 8.38E 05 -1.06E-04~ -3.89E-05 NO DATA 3.80E 05 1.51E 05 1.06E-06 CS-138 5.82E 08 1.07E-07 5.58E-08 NO DATA 8.28E-08 9.84E-09 3.38E-11 BA-139 1.67E 10 1.18E-13 4.87E-12 NO DATA 1.11E-13 8.08E-07 8.06E 07
)
BA-140 6.84E-06 8.38E-09 4.40E-07 NO DATA 2.85E-09 2.54E-04 2.86E 05 BA-141- 1.78E-11 1.32E-14 5.93E-13 NO DATA 1.23E 14 4.11E 07 9.33E 14 BA-142 4.62E-12 4.63E-15 2.84E 13 NO DATA 3.92E 15 2.39E 07 5.99E.20 IA-140 5.99E-08 2.95E-08 7.82E-09 NO DATA NO DATA 2.68E-05 6.09E-05 IA-142 1.20E-10 5.31E-11' 1.32E-11 NO DATA NO DATA 1.27E 06 1.50E 06 CE-141 3.55E 06' 2.37E 06 2.71E-07 NO DATA 1.11E 06 7.67E 05 1.58E-05 CE-143 3.32E-08 2.42E-08 2.70E 09 NO DATA 1.08E-08 1.63E-05 3.19E-05 CE-144 6.11E-04 2.53E-04 3.28E-05 NO DATA 1.51E-04 1.67E 1.08E-04 PR 143 -1.67E 06 6.64E 8.28E 08 NO DATA 3.86E-07 6.04E-05 2.67E 05 PR-144 5.37E-12 2.20E-12 2.72E-13 NO DATA l.26E-12 2.19E-07 2.94E-14 ND-147 9.83E 07 1.07E 06 6.41E 08 NO DATA 6.28E-07. 4.65E-05 2.28E 05 U-187 1.50E 09 1.22E-09 4.29E-10 NO DATA NO DATA 5.92E-06 2.21E-05 NP 239 4.23E-08 3.99E-09 2.21E-09 NO DATA 1.25E-08 8.11E-06 1.65E-05
- 3.52 X 10 -06
- 'Less than 10~24 CLINTON-1 3-56 Rev 5-2/89
CPS-ODCM-l Table 3.5-4 INHALATION DOSE FACTORS FOR ADULT - (DFAi)a ,.
(mrem per pCi inhaled)
THYROID KIDNEY LUNG GI-LLI NUCLIDE BONE LIVER T. BODY 1.58E-07 1.58E-07 1.58E 07 1.58E 07 1.58E-07 1.58E-07 H3 NO DATA 4.26E-07 4.26E 07 C-14 2.27E 06* 4.26E 07 4.26E-07 4.26E-07 4.26E-07 1.28E-06 1.28E-06 1.28E 06 1.28E-06 1.28E 06 1.2SE 06 NA-24 1.28E-06 9.64E 06 6.26E-06 NO DATA NO DATA NO DATA 1.08E 05 P 32 1.65E-04 4.15E 07 NO DATA NO DATA 1.25E-08 7.44E 09 2,85E-09 1.80E-06 CR-51 9.67E 06
,206 54 NO DATA 4.95E-06 7.87E-07 NO DATA 1.23E 03 1.75E-04 i
2.29E-11 NO DATA 1.63E-10 1.18E-06 2.53E-06 MN-56 NO DATA 1.55E-10 2.12E-06 4.93E-07 NO DATA NO DATA 9.01E 06 7.54E-07 FE 55 3.07E 06 2.35E 05 FE 59 1.47E 06 3.47E-06 1.32E 06 NO DATA NO DATA 1.27E 04 1.98E-07 2.59E 07 NO DATA NO DATA 1.16E 04 1.33E 05 CO-58 NO DATA 3,56E-05 NO DATA 1.44E-06 1.85E-06 NO DATA NO DATA 7.46E-04 CO-60 2,23E 05 1.67E-06 5.40E 05 3.93E-06 1.81E 06 NO DATA NO DATA NI-63 1.14E-11 NO DATA NO DATA 7.00E-07 1.54E 06 ll 37 65 1.92E-10 2.62E-11 1.83E-10 7.69E-11 NO DATA 5.78E-10 8.48E-07 6.12E 06 CU-64 NO DATA 5,82E-06 NO DATA 8.62E 06 1.08E-04 6.68E 06 2N-65 4.05E-06 1.29E-05 8.14E-12 5.65E 13 NO DATA 5.27E-12 1.15E-07 2.04E-09 Zlf-69 4.23E-12 2.90E 08 NO DATA 3.01E-08 NO DATA NO DATA NO DATA BR-83-- .NO DATA NO DATA NO DATA 2 -. 05 E- 13 BR-84 'NO DATA NO DATA 3.91E 08 NO DATA NO DATA 1.60E 09 NO DATA NO DATA NO DATA LT E-24**
BR-85 NO DATA 1.69E-05 7.37E-v6 NO DATA NO DATA NO DATA 2.08E 06 RB-86 NO DATA 4.18E-19 4.84E-08 2.41E-08 NO DATA NO DATA NO DATA RB.-88 NO DATA 3.20E-08' 2.12E-08 NO DATA NO DATA NO DATA 1.16E 21 RB NO DATA-NO DATA 1.09E-06 NO DATA NO DATA 1.75E-04 4.37E 05 SR-89 3.80E-05 9.02E-05^
SR-90 1~.24E-02 NO DATA 7.62E 04 NO DATA NO DAT/. 1.20E-03 CLINTON-1 3-57 Rev.5-2/89
CPS-ODCM l
T.3ble 3.5-4 (continued)
INHALATION DOSE FACTORS FOR ADULT - (DFA1)a (mrom per pCi inhaled)
NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI LLI SR 91 7.74E 09 NO DATA 3.13E 10 NO DATA NO DATA 4.56E-06 2.39E 05 SR 92 8.43E-10 NO DATA 3.64E 11 NO DATA NO DATA 2.06E-06 5.38E 06 Y 90 2.61E 07 NO DATA 7.01E-09 NO DATA NO DATA 2.12E 05 6.32E-05 Y-91m 3.26E-11 NO DATA 1.27E 12 NO DATA NO DATA 2.40E 07 1.66E 10 Y 91 5.78E-05 NO DATA 1.55E 06 NO DATA NO DATA 2.13E 04 4.81E 05 -
Y-92 1.29E-09 NO DATA 3.77E-11 NO DATA NO DATA 1.96E 06 9.19E 06 Y-93 1.18E 08 NO DATA 3.26E-10 NO DATA NO DATA 6.06E-06 5.27E 05 ZR 95 1.34E-05 4.30E 06 2.91E 06 NO DATA 6.77E-06 2.21E-04 1,88E-05 ZR-97 1.21E-08 2.45E 09 1.13E NO DATA ' 3.71E-09 9.84E 06 6.54E-05 NB 95 1.76E-06 9.77E-07 5.26E-07 NO DATA 9.67E-07 0.31E 05 1.30E 05 MO-99 NO DATA 1.51E-08 2.87E 09 NO DATA 3.64E 08 1.14E-05 3.10E 05 TC 99m 1.29E-13 3.64E-13 4.63E-12 NO DATA 5.52E-12 9.55E-08 5.20E 07 TC-101 5.22E-15 7.52E-15 7.38E 14 NO DATA 1.35E-13 4.99E-08 1.36E-21 RU-103 1.91E-07 NO DATA 8.23E 08 NO DATA 7.29E-07 6,31E-05 1.38E 05 RU-105 9.88E-11 NO DATA 3.89E-11 NO DATA 1.27E 10 1.37E 06 6.02E 06 RU 106 8.64E-06' NO DATA 1,09E-06 NO DATA 1.67E-05 1.17E-03 1.14E-04 -
AC-110m 1.35E 06 1.25E-06 7.43E 07 NO DATA 2.46E-06 5.79E-04 3.78E-05 TE-125m 4.27E 07 1.98E-07 5.84E-08 1.31E 07 1.55E-06 3.92E-05 8.83E-06 TE 127m 1.58E-06 7.21E-07 1.96E 07 4.11E-07 5.72E-06 1.20E-04 1.87E-05 TE 127 1.75E-10 8.03E 11 3.87E-11 1.32E-10 6.37E-10 8.14E-07 7.17E-06 TE-129m 1.22E 06 5.84E-07 1.98E-07 4.30E-07 4.57E-06 1.45E-04 4.79E 05 TE-129 6.22E 12 2.99E 12 1.55E 12 4.87E-12 2.34E-11 2.42E-07 1.96E-08 TE-131m -8.74E-09 5.45E-09 3.63E-09 6.88E-09 3.86E-08 1.82E-05 6.95E 05 TE-131 1.29E 12 7.44E-13 4.49E 13 1.17E-12 5.46E 12 1.74E-07 2.30E-09 TE 132 3.25E-08 2.69E-08 2.02E 08 2.37E-08 1.82E-07 3.60E-05 6.37E-05 1 130 5.72E 07 1.68E 06 6.60E C 1.42E-04 2.61E 06 NO DATA 9.61E.07 I-131 3.15E-06 4.47E-06 2.56E-06 1,49E-03 7.66E-06 NO DATA 7.85E-07 CLINTON-1 3-58 Rev.1-11/85 l
CPS-UUCM Table 3.5-4 (continued)
INHALATION DOSE FACTORS FOR ADULT - (DFA1)a (mrem por pci inhaled)
T. BODY THYROID KIDNEY LUNG CI LLI NUCLIDE- BONE LIVER 4.07E-07 1.45E 07 1.43E-05 6.48E 07 NO DATA 5.08E 08 I-132 1.45E 07 1.85E 06 5.65E 07 2.69E-04 3.23E 06 NO DATA 1.11E-06 I 133 1.08E 06 2.16E 07 7.69E 08 3.73E-06 3.44E 07 NO DATA 1.26E 10 I 134 8.05E 08 8.73E-07 3.21E 07 5.60E 05 1.39E 06 NO DATA 6.56E-07 I 135 3.35E 07 1.22E 05 1.30E 06 CS-134 4.66E 05 1.06E-04 9.10E 05 NO DATA 3.59E 05 1.83E 05 1.38E 05 NO DATA 1.07E 05 1.50E 06 1.46E 06 :
CS-136 4.88E 06 7.76E 05 5,35E 05 NO DATA 2.78E 05 9.40E 06 1.05E 06 CS-137 5.98E-05 2.33E 13 CS-138 4.14E 08 7.76E-08 4.05E 08 NO DATA 6.00E-08 6.07E 09 8.32E-14 3.42E-12 NO DATA 7.78E 14 4.70E 07 1.12E 07 BA-139 1.17E-10 2.09E-09 1.59E 04 2,73E-05 BA 140 4.88E 06 6.13E-09 3.21E-07 NO DATA 9.41E 15 4.20E 13 NO DATA 8.75E-15 2.42E 07 1.45E 17
- BA-141 1.25E-11 1.96E-26 BA-142 3.29E-12 3.38E-15 2.07E-13 NO DATA 2.86E-15 1.49E-07 2.17E-OR 5.73E 09 NO DATA NO DATA 1.70E 05 5.73E 05 LA-140 4.30E-08 2.64E-07 1A-142 8.54E-11 3.88E-11 9.65E 12 NO DATA NO DATA 7.91E-07 1.69E 06 1.91E-07 NO DATA 7.83E 07 4.52Es05 1.50E 05 CE-141 2.49E-06 1.72E-08 1.91E-09 NO DATA 7.60E 09 9.97E 06 2.83E-05 CE-143 2.33E-08 1.02E-04 4.29E 04 1.79E-04 2.30E 05 NO DATA 1.06E-04 9.72E 04
.CE-144 3.51E 05 2.50E 05 PR-143 1.17E 4.09E 07 5.80E 08 NO DATA 2.!OE 07 1.56E 12 1.91E-13 NO DATA 8.81E-13 1,27E-07 2.69E-18
'PR-144 3.76E 2,76E 05 2.16E 05 ND-147 6.59E-07 7.62E 07 4.56E-08 NO DATA 4.45E 07 8.85E-10 3.10E 10 NO DATA NO DATA 3.63E-06 1.94E-05
.W-187 1.06E-09 1.55E-09 NO DATA 8.75E-09 4.70E-06 1.49E-05 NP-239 2.87E 08 2.82E-09
- 2.27 X 10-06
- Less than 10-24 1
CLINTON-1 3-59 Rev.5-2/89
CPS-ODCM TABLE 3.5-5 GROUND PLANE DOSE FACTORS - DFGi (mrem /hr per pCi/,')
ELEMENT TOTAL BODY EZJJf.
H-3 0.0 0.0 C-14 0.0 0.0 Na 24 2.50E-08* 2.90E 08 P-32 0.0 0.0 Cr 51 2.20E-10 2.60E-10 Mn 54 5.80E-09 6.80E-09 Kn 56 1.10E-08 1.30E-08 Fe-55 0.0 0.0 Fe-59 8.00E-09 9.40E 09 Co-58 7.00E 09 8.20E-09 Co 60 1.70E-08 2.00E-08 Ni-63 0.0 0.0 Ni-65 3.70E-09 4.30E 09 Cu-(4 1.50E-09 70E 09 Zn 65 4.00E-09 4.60E-09 Zn-69 0.0 0.0
-Br 83 6.40E-11 9.30E 11 Br-84 1.20E-08 1.40E-08 Br 85 0.0 0.0 Rb-86 6.30E-10 7.20E-10 Rb 88 3.50E-09 4.00E-09 Rb 89 1.50E-08 1.80E-08 Sr 89 5.60E-13 6.50E-13 Sr-91 7.10E-09 8.30E-04 Sr 92 9.00E-09 1.00E-08 Y 90 2.20E 12 2.60E-12 Y-91m 3.80E-09 4.40E-09 Y-91 2.40E-11 2.70E 11 Y 92 1.60E-09 1.90E-09 Y 93 5.70E 10 7.80E-10 Zr 95 5.00E-09 5.80E 09 2r-97 5.50E-09 6.40E-09 Nb-95 5.10E-09 6.00E-09 Mo-99 1.90E-09 2.20E-09 Tc-99m 9.60E-10 1.10E-09 Tc-101 2.70E-09 3.00E-09 Ru-103 3.60E-09 4.20E-09 Ru-105 4.50E-09 5.10E 09 Ru-106 1.50E-09 1.80E-09 Ar-110m 1.80E-08 2.10E-08 CLINTON-1 3-60 Rev 5-2/89
- CPS-ODCM-Table 3.5-5-(Continued)
GROUND PLANE' DOSE FACTORS - DFGi (mrem /hr per pCi/m2 )-
ELEMENT TOTAL BODY SKU{
- Te-125m 3.50E-11 4.80E-11 Te 127m 1.10E 12 1.30E 12
. Te-127 1.00E 11 1.10E-11 Te-129m' 7.70E-10 9.00E-10 Te-129 7.10E-10 8.40E 10 Te-131m 8.40E 09 9.90E 09 Te-131- 2.20E 09 2.60E-06 Te-132 1.70E-09 2.00E-09
-I-130- -1.40E 08 1.70E-08 I-131 2.80E-09 3.40E 09 I 132. 1.70E-08 2.00E-08 I-133' 3'.70E-09 4.50E-09
- I-134 1.60E-08 1.90E 08 I-135_ .1.20E-08 1.40E-08 Cs-134 1.20E-08 1.40E-08
.cs-136 1.50E-08 1.70E-08 Cs-137 4.20E 09 4.90E 09
.Cs-138 2.10E 08 2.40E-08 LBa 139. 2.40E-09 2.70E-09
~Ba-140 2.10E-09 2.40E-09 Ba-141 4.30E 09 4.90E-09 }'
Ba,-142 7.90E 9.00E 09 La-140 1.508-08 1.70E 08 La-142 1.50E-08 1.80E-08 Ce-141 5.50E-10 6.20E-10
.Ce-143. .2.20E-09 2.50E 09 Ce-144 3.20E-10 3.70E-10 Pr-143 0.0 0.0 Pr 144 2.00E-10 2.30E-10 Nd-147. 1.00E 09 1.20E-09 -
,U-187 -
3.10E 3,60E-09 Np-23S 9.50E-10 1.10E-09
- 2.50;X 10-08 i
CLINTON-1 3-61 Rev.5-2/89 mt-
CPS-ODCM TABLE 3.5-6 INGESTION DOSE FACTORS FOR INFANT - ( DFLi) a (mrem per pCi ingested)
NUCLIDE Eqt{g LIVER T. BODY. TKiDalp KIDNEY lEIG GI-LL1 i H3 NO DATA 3.08E 07 3.08E 07 3.08E-07 3.08E-07 3.08" 07 3.08E 07 C-14 2.37E-05* 5.06E-06 5.06E 06 5.06E-06 5.06E-06 5.06E 06 5.06E 06 NA 24 1.01E-05 1.01E-05 1.01E-05 101E 05 1.01E 05 1.01E-05 1.01E-05 P-32 1.70E 03 1.00E-04 6.59E 05 NO DATA NO DATA NO DATA 2.30E 05 CR-51 NO DATA NO DATA 1.41E-08 9.20E 09 2.01E 09 1.79E 08 4.11E 07 MN 54 NO DATA 1.99E-05 4.51E 06 NO DATA 4.41E-06 NO DATA 7.31E-06 MN-56 NO DATA 8.18E-07 1.41E-07 NO DATA 7.03E-07 UO DATA 7.43E-05 FE-55 1.39E-05 8.98E-06 2.40E 06 NO DATA NO DATA 4.39E-06 1.14E-06 FE-59 3.08E 05 5.38E-05 2.12E-05 NO DATA NO DATA 1.59E-05 2.57E-05 Co-58 NO DATA 3.60E-06 8.98E 06 NO DATA NO DATA NO DATA 8.97E-06 CO-60 NO DATA 1.08E-05 2.55E-05 NO DATA NO DATA NO DATA 2.57C 05 NI-63 6.34E-04 3.92E-05 2.20E-05 NO DATA NO DATA NO DATA 1.95E 06
) NI-65 4.70E 06 5.32E 07 2.42E 07 NO DATA NO DATA NO DATA 4.05E 05 CU-64 NO DATA 6.09E-07 2.82E 07 NO DATA 1.03E-06 NO DATA 1.25E-05 ZN 65 1.84E-05 6.31E-05 2.91E-05 NO DATA 3.06E-05 NO DATA 5.33E 05 ZN 69 9.33E-08 1.68E-07 1.25E-08 NO DATA 6.98E 08 NO DATA 1.37E 05 BR-83 NO DATA NO DATA 3.63E-07 NO DATA ??O DATA NO DATA LT E-24** '
BR-84 NO DATA NO DATA 3.82E-07 NO DATA NO DATA NO DATA LT E-24 BR-85 NO DATA NO DATA 1.94E 08 NO DATA NO DATA NO DATA LT E 24 RB-86 NO DATA 1.70E-04 8.40E-05 NO DATA NO DATA NO DATA 4.34E-06 RB-88 NO DATA 4.98E-07 2.73E-07 NO DATA NO DATA NO DATA 4.85E 07 RS-89 NO DATA 2.86E-07 1.97E-07 NO DATA NO DATA NO DATA 9.74E-08 SR-89 2.51E-03 NO DATA 7.20E-05 NO DATA NO DATA NO DATA 5.16E 05 SR-90 1.85E 02 NO DATA 4.71E-03 NO DATA NO DATA NO DATA 2.31E-04 SR 91 5.00E-05 NO DATA 1.81E-06 NO DATA NO DATA NO DATA 5.92E-05 SR-92 1.92E 05 1' DATA 7.13E 07 NO DATA NO DATA NO DATA 2.07E 04 Y-90 8.69E-08 h 5.TA 2.33E-09 NO DATA NO DATA NO DATA 1.20E 04 CLINTON-1 3-62 Rev.1-11/85 l
l
CPS-ODCM.
TABLE 3.5-6 (continued)
INGESTION DOSE FACTORS FOR INFANT - (DFLi )a (mrem per pCi ingested)
LIVER T. BODY THYROID RIDNEY LUEQ G.I-LLI MUCLIDE EQHE 2.76E-11 NO DATA NO DATA NO DATA 2.70E-06
.Y 91m 8.10E 10 NO DATA 3.01E-08 NO DATA NO DATA NO DATA 8.10E-05 Y-91 1.13E 06 NO DATA NO DATA 1.46E-04 ,
2.15E-10 NO DATA NO DATA Y-92 7.65E-09 NO DATA 6.62E 10 NO DtTA NO DATA NO PATA 1.92E 04 Y 93 2.43E 08~ NO DATA 3.56E-08 NO DATA 5.41E-08 NO DATA 2.50E-05 ZR 95 2.06E-07 5.02E 08 1.62E-04 1.16E-09 NO DATA 2.56E-09 NO DATA l ZR 97 1.48E-08 2.54E-09 l
1.00E 08 NO DATA 1.24E-08 NO DATA 1.46E-05 NB 95 4.20E-08 1.73E-08 1.12E 05 6.63E 06 NO DATA 5.08E-05 NO DATA
.MO-99 NO DATA 3.40E-05 1.15E 06 :
3.96E-09' 5.10E 08 NO DATA 4.26E 08 2.07E 09 TC-99m 1.92E-09 3.40E-08 1.56E 09 4.86E 07 TC-101 2.27E-09 2.86E 09 2.83E 08 NO DATA 1.80E 05 4.95E-07 NO DATA 3.08E-06 NO DATA RU-103- 1.48E-06 NO DATA 5.41E-05 4.58E-08 NO DATA 1.00E-06 NO DATA RU-105 1.36E-07. NO DATA 2.85E-05 NO DATA 1.83E-04 RU-106 2.41E-05 NO DATA 3.01E-06 NO DATA 3 77E-05
-4.81E-07 NO DATA 1.04E-06 NO DATA AG-110m 9.96E-07 7.27E-07 NO DATA 1.llE-05 7.79E-06 3 .15 E'- 06 7.84E-06 NO DATA TE 125m- 2.33E-05 7.08E-06 1.69E-05 1.44E 04 NO DATA 2.36E 05
-TE-127m 5.85E-05 1.94E-05 2.10E 05 1.00E 06 3.35E-07 2.15E 07 8.14E-07 2.44E-06 NO DATA
.TE-127 2.50E-04 NO DATA 5.97E-05 TE-129m 1.001-04 3.43E 05 1.54E-05 3.84E 05 2.38E-07 7.075-07 NO DATA 2.27E-05 TE-129 2.84E-07 9.79E-08 6.63E 08 1.24E-05 4.21E-05 NO DATA 1.03E-04 TE-131m' 1.52E-05 6.12E-06 5.05E 06 7.11E-06 4.94E-08 1.57E-07 4.50E-07 No DATA
-TE 137. 1.76E-07 6.50E-08 1.52E-05 6.44E-05 NO DATA 3.81E-05 TE-132 2.08E-05 1.03E-05 9.61E-06 1.48E-03 1.45E-05 No DATA 2.83E-06 I-130 6.00E-06 1.32E 5.30E-06 1.39E-02 4.94E-05 NO DATA 1.51E-06
.I-131- 3.59E 05 4.23E-05 1.86E.05 I
' 11.58E-04 3.76E-06 NO DATA 2.73E 06 I-132i 1.66E-06 3.37E 06 1.20E-06 3.08E-06 3.31E-03 2.14E-05 NO DATA
-I-133 .1.25E 05 1.8?E-05 5.33E-06 1.84E-06 6.33E-07 4.15E 05 1.99E-06 NO DATA I-134 8.69E-07 1.78E-06 3-63 Rev 1-11/85
=CLINTON-1
CPS-ODCM TABLE 3.5-6 (continued).
INGESTION DOSE FACTORS FOR INFANT - (DFLi )a (mrem per pCi ingested)
NUCLIDE- SQl!E LIVER T. BODY THYROID KIDNEY LIR!G GI-LLI I-135 3.64E-06~ 7.24E-06 2.64E-06 6.49E-04 8.07E-06 NO DATA 2.62E 06 CS 134- 3.77E-04' 7.03E-04 7.10E-05 NO DATA 1.81E 04 7.42E 05 1.91E 06
.CS-136 4.59E-05 1.35E 04 5.04E-05 NO DATA 5.38E-05 1.10E-05 2.05E 06 CS 137 5.22E-04 6.11E 04 4.33E-05 NO DATA 1.64E 04 6.64E 05 1.91E 06 CS-138 4.81E-07 7.82E-07 3.79E-07 NO DATA 3.90E-07 6.09E-08 1.2SE 06 BA-139 8.81E-07 5.84E-10 2.55E-08 NO DATA 3.51E-10 3.54E-10 5.53E 05 BA-140- 1.71E 04 1.71E 8.81E-06 NO DATA 4.06E-08 1.05E 07 4.20E 05 BA 141. 4.25E-07 2.91E-10 1.34E-08 NO DATA 1.75E-10 1.77E-10 5.19E 06 BA-142 1.84E 07 1.53E-10 9.06E-09 NO DATA 8.81E 11 9.26E-11 7.59E 07 IA-140- 2.11E-08 8.32E-09 2.14E-09 NO DATA NO DATA NO DATA 9.77E 05 IA-142 1.10E-09 4.04E-10 9.67E-11 NO DATA NO DATA NO DATA 6.86E 05 CE-141 7.87E-08 4.80E 08 5.65E 09 NO DATA 1.48E-08 NO DATA .': . 48 E - 0 5
'i CE-143 1.48E-08 9.82E 06 1.12E-09 NO DATA 2,86E-09 NO DATA 5.73E-05 CE-144' 2.98E 06 1.22E 06 1.67E-07 NO DATA 4.93E-07 NO DATA 1.71E-04 PR-143 8.13E-08 3.04E 08 4.03E-09 NO DATA 1.13E-08 NO DATA 4.29E 05 PR-144 2.74E-1C 1.06E-10 1.38E NO DATA 3.84E-11 NO DATA 4.93E-06 ND 147. 5.53E-08 5.68E-08 3.48E-09 NO DATA 2.19E-08 NO DATA 3.60E-05 W-187. 9.03E-07 6.28E 07 2.17E 07 MO LTA NO DATA NO DATA 3.69E NP-239 1.11E-08 9.93E 10 5.61E-10 NO DATA 1.98E-09 NO DATA '2.87E-05
.
- 2.37 X 10-05
- Less than 10~24 CLINTON-1 3-64 Rev.1-11/85
CPS-ODCM TABLE 3.5-7 INGESTION DOSE FACTORS FOR CHILD - (DFLi )a (mrem per pCi ingested)
LIVER T. BODY THYROID; KIDNEY LE{ft CI-LLI NUCLIDE EQE H3 NO DATA 2.03E 07 2.03E-07 2.03E-07 2.03E 07 2.03E-07 2.03E-07 C 14 1.21E-05* 2.42E-06 2.42E 06 2.42E 06 2 42E 06 2.42E-06 2.42E 06 NA-24 5.80E-06 5.80E 06 5.80E 06 5.80E-06 5.80E 06 5.80E 06 5.80E 06 P 32 8.25E-04 3.86E 3.18E-05 NO DATA NO DATA NO DATA 2.28E 05 CR 51 NO DATA NO DATA 8.90E-09 4.94E-09 1.35E-09 9.02E 09 4.72E-07 MN-54 NO DATA 1.07E 05 ' 85E-06
. NO DATA 3.00E-06 NO DATA 8.98E-06 MN-56 NO DATA 3.34E-07 7.54E-08 NO DATA 4.04E-07 NO DATA 4.84E 05 FE 55 1.15E-05 6.10E 06 1.89E-06 NO DATA NO DATA 3.45E-06 1.13E 06 FE-59 1.65E-G5 2.67E-05 1.33E 05 NO DATA NO DATA 7.74E 06 2.78E-05 CO-58 NO DATA 1.80E-06 5.51E 06 NO DATA NO DATA NO DATA 1.05E 05
-CO 60 NO DATA 5.29E-06 1.56E-05 NO DATA NO DATA NO DATA 2.93E-05 NI 5.38E-04 2.88E-05 1.83E-05 NO DATA NO DATA NO DATA 1.94E-06 NI-65 2.22E-06 2.09E-07 1.22E-07 NO DATA NO DATA NO DATA 2.56E-05 #
CU-64 NO DATA 2.45E-07 1.48E-07 NO DATA 5.92E-07 NO DATA 1.15E 05 ZN-65 1.37E-05 3.65E 05 2.27E-05 NO DATA 2.30E 05 NO DATA 6.41E-06 4.38E-08 6.33E-08 5.85E 09 NO DATA 3.84E-08 NO DATA 3.99E-06 ZN 69 NO DATA NO DATA 1.71E-07 NO DATA NO DATA NO DATA LT E 24**
BR-83 NO DATA NO DATA 1.98E 07 NO DATA NO DATA NO DATA LT E-24 BR-84 NO DATA NO DATA 9.12E-09 NO DATA NO DATA NO DATA LT E-24 BR-85 NO DATA 6.70E-05 4.12E-05 NO DATA NO DATA NO DATA 4.31E-06 RB-86 RB-88 NO DATA 1.90E 07 1.32E 07 NO DATA NO DATA NO DATA 9.32E-09 NO DATA 1.17E-07 1.04E-07 NO DATA NO DATA NO DATA 1.02E-09 RB-89
'1.32E-03 NO DATA 3.77E 05 NO DATA NO DATA NO DATA 5.11E-05 SR-89 1.70E-02 NO DATA 4.31E-03 NO DATA NO DATA NO DATA 2.29E-04 SR 90 SR-91 2.40E-05 -NO DATA 9.06E 07 NO DATA NO DATA NO DATA 5.30E-05 9.03E 06 NO DATA 3.62E-07 NQ DATA NO DATA NO DATA 1.71E-04 SR-92 4.11E-08 1.10E-09 NO DATA NO DATA NO DATA 1.17E-04 Y-90 NO DATA L CLINTON-1 3-65 Rev.5-2/89
CPS-CDCM TABLE:3.5-7 (continued) 1NGESTION DOSE FACTORS FOR CHILD - (DFLi )a (mrem per pCi ingested)
'NUCLIDE- EQJ.E LEER T. BODY- THYROID KIDNEY kg{Q GI-LLI Y-91m 3.82E-10 NO DATA 1.39E-11 NO DATA NO DATA NO DATA 7.48E 07 Y 6.02E 07 NO DATA 1.61E-08 NO DATA NO DATA NO DATA 8.02E 05 1.04E 04 Y-92 3.60E 09 NO DATA 1.03E 10 NO DATA NO DATA NO DATA Y 93 1.14E 08 NO DATA 3.13E-10 NO DATA NO DATA NO DATA 1.70E 04 ZR-95 1.16E 07 2.55E-08 2.27E-08 NO DATA 3.65E-08 NO DATA 2.66E 05 ZR 97 6.99E-09 1.01E-09 5.96E-10 NO DATA 1.45E 09 NO DATA 1.53E-04 NB-95 2.25E-08 8.76E-09 6.262-09 NO DATA 8.23E-09 NO DATA 1.62E 05 MO-99 NO DATA 1.33E-05 3.29E-06 NO DATA 2.84E 05 NO DATA 1.10E 05 TC-99m 9.23E-10_ 1.81E-09 3.00E-08 NO DATA 2.63E-08 9.19E 10 1.03E 06 TC-101 1.07E-09 1.12E-09 1.42E 08 NO DATA 1.91E-08 5.92E 10 3.56E 09 RU-103 7.31E-07 NO DATA 2.81E-07 NO DATA 1.84E-06 NO DATA 1.89E 05 RU-105 '6.45E-08 NO DATA - 2.34E-08 NO DATA 5.67E-07 NO DATA 4.21E-05 RU 106 1,17E 05 NO DATA 1.46E-06 NO DATA 1.58E-05 NO DATA 1.82E 04 AG-110m 1.39E 3.64E-07 2.91E-07 NO DATA 6.78E-07 NO DATA 4.33E-05 TE-125m 1.14E-05 3.09E-06 1.52E-06 3.20E-06 NO DATA NO DATA 1.10E-05 TE-127m 2,89E-05 7.78E-06 3.43E 06 6.91E-06 8.24E-05 NO DATA 2.34E-05
.-TE 127 .
4,71E 07 --1.27E 07 1.01E 07 3.26E 07 1.34E-06 NO DATA 1.84E 05 TE-129m 4.87E 05 1.36E-05 7.56E-06 1.57E-05 1.43E 04 NO DATA 5.94E-05 TE-129 1.34E-07 3.74E-08 3.18E 08 9.56E-08 3.92E-07 NO DATA _8.34E 06 TE 131m 7,20E-06 2.49E-06 -2.65E-06 '5.12E-06 2.41E 05- NO DATA 1.01E-04 TE-131 8.30E-08 2.53E-08 2,47E-08 6.35E-08 .2.51E 07 NO DATA 4.36E-07 TE.132 1.01E-05 4.47E-06 5.40E 06 fi.51E-06 4.15E-05 NO DATA -4.50E 05
'I-130 2.92E-06 5.90E 06 '3.04E-06 6,50E-04 8.82E-06 NO DATA 2.76E-06 I-131 1.72E-05 1.73E-05 9.832 06 5.72E-03 2.84E-05 NO DATA 1.54E-06 I 132 8.00E-07 1.47E-06 6.76E-07 6.82E 05 2.25E-06 NO DATA 1.73E 06 I-133- 5.92E-06 7.32E 06 2.77E-06 _1_. 3 6 E - 03 1.22E-05 NO DATA 2.95E-06 I-134 4.19E 07 7.78E 07 3.58E-07 1.79E-05 1.19E 06 NO DATA 5.16E-07 CLINTON-1 3-66 Rev.5-2/89 n
CPS-ODCM j TABLE 3.5-7 (continued ( l INGESTION DOSE' FACTORS FOR CHILD - (DFLi )a (mrem per pCi 1..gested) i NUCLIDE 3,Qy_E LIVER T. BODY THYROID KIDNEY Lk31Q GI-LLI 1-135 1.75E 06 3.15E 06 1.49E 06 2.79E 04 4.83E 06 NO DATA 2.40E 06 CS-134 2.34E-04 3.84E 04 8.10E 05 NO DATA 1.19E 04 4.27E 05 2.07E 06 I CS-136 2.35E 05 6.46E 05 4.18E-05 NO DATA 3.44E-05 5.13E-06 2.27E 06 l l
CS-137 3.27E-04 3.13E-04 4.62E-05 NO DATA 1.02E 04 3.67E-05 1.96E 06 l CS-138 2.28E-07. 3.17E-07 2.01E-07 NO DATA 2.23E-07 2.40E-08 1.46E-07 BA-139. 4.14E 07 2.21E-10 1.20E-08 NO DATA 1.93E-10 1.30E-10 2.39E 05 l
BA-140 8.31E 05 7.28E-08 4.85E 06 NO DATA 2.37E 08 4.34E-08 4.21E 05.
RA-141 2.00E-07 1.12E-10 6.51E-09 NO DATA 9.69E-11 6.58E-10 1.14E-07 BA-142 8.74E 08 6.29E-11 4.88E-09 NO DATA 5.09E-11 3.70E 11 1.14E 09 l
ZA-140 1.01E-08 3.53E-09 1.10E-09 NO DATA NO DATA NO DATA 9.84E405 LA-142 5.24E-10 1.67E-10 5.23E-11 NO DATA NO DATA NO DATA 3.31E 05
.CE-141 8.97E-08 1.98E-08 2.94E-09 NO DATA 8.68E-09 NO DATA 2.47E-05 CE-143 6.99E-09 3.79E-06 5.49E-10 NO DATA 1.59E-09 NO DATA 5.55E 05 3 CE-144 2.08E-06 6.52E 07 1.11E-07 NO DATA 3.61E 07 NO DATA 1.70E-04 PR-143 3.93E-08 1.18E-08 1.95E-09 NO DATA 6.39E-09 NO DATA 4.24E 05 PR-144 1.29E 10 3.99E-11 6.49E-12 NO DATA 2.11E-11 NO DATA 8.59E-08 NU-147 2.79E-08 2.26E-08 1.75E 09 NO DATA 1.24E-08 NO DATA 3.58E-05 U-187. 4.29E-07 2.54E-07 1.14E-07 NO DATA NO DATA NO DATA 3.57E 05 NP'-239 5 . 2 5 E'- 09 3.77E-10 2.65E-10 NO DATA 1.09E-09 NO DATA 2.79E 05
- 1 21 X 10-05
- Less than 10-24 l
l-l t.
CIINTON-1 3-67 Rev.6-12/89 I
I
} u - - ew.. - - .ai m .p. _Jp,.. ,it(.A CPS-ODCM TABLE 3.5-6 INGESTION DOSE FACTORS FOR TEEN - (DFLi )a (mrem per pCi ingested)
. E,CLIDE E LIVER T. BODY THYROID KIDNEY M SIdL1 H-3 NO DATA 1.06E 07 1.06E-07 1.06E-07 1.06E-07 1.06E-07 1.06E 07
-C 14 4.06E 06* 8.12E-07 8.12E 07 8.12E-07 8.12E 07 8.12E-07 8.12E-07
~NA-24 2.30E-06 2.30E 06 2.30E-06 2.30E-06 2.30E-06 2.300-06 2.30E-06 P 32 2.76E 1.712-05 1.07E 05 NO DATA NO DATA NO DATA 2.32E-05
-CR 51 NO DATA NO DATA. 3.60E-09 2.00E-09 7.89E-10 5.14E.79 6.05E-07 MN-54 NO DATA 5.90E-06 1.17E-06 NO DATA 1.76E-06 NO DATA 1.21E 05 MN-56 NO DATA 1.58E-07 2.81E-08 NO DATA 2.00E 07 NO DATA 1.04E-05 FE 55 3.78E-06 2.68E-06 6.25E 07 NO DATA - NO DATA 1.70E 06 1.16E-06 FE-59 5.87E-06 1.37E-05 5.29E-06 NO DATA NO DATA 4.32E-06 3.24E 05 CO-58 NO DATA 9.72E 07 2.24E-06 NO DATA NO DATA NO DATA 1.34E-05 CO-60 NO DATA 2.81E-06 6.33E-06 NO DATA NO DATA NO DATA 3.66E-05 NI-63 1;77E-04 1.25E-05 6.00E-06 NO DATA NO DATA NO DATA 1.99E-06
) NI-65 CU 64 7.49E-07
- NO DATA 9.57E-08 1.15E-07 4.36E 08 5.41E-08 NO DATA NO DATA NO DATA 2.91E 07 NO DATA NO DATA 5.19E-06 8.92E-06 ZN-65 5.76E-06 2.00E-05 9.33E 06 NO DATA 1.28E-05 NO DATA 8.47E-06 ZN-69 1.47E-08 2.80E-08 1.96E-09 NO DATA 1.83E-08 NO DATA 5.16E 08 BR-83 NO DATA NO DATA 5.74E-08 NO DATA NO DATA NO DATA LT E-24**
BR-84 NO DATA NO DATA- 7.22E-08 NO DATA NO DATA NO DATA LT E-24 BR-85 NO DATA NO DATA 3.05E-09 NO DATA NO DATA NO DATA LT E-24 RB-86 NO' DATA 2.98E-05 1.40E-05 NO DATA NO DATA NO DATA 4.41E-06 RB-88 NO DATA 8.52E-08 4.54E 08 NO DATA NO DATA NO DATA 7.30E-15 RB-89 NO DATA 5.50E-08 3.89E-08 NO DATA NO DATA NO DATA 8.43E 17 SR-89 4.40E-04 NO DATA 1.26E-05 NO DATA NO DATA NO DATA 5.24E-05 SR-90 - 8.30E-03 NO DATA 2.05E-03 NO DATA NO DATA NO DATA 2.33E-04 SR-91 - 8.07E 06 NO DATA 3.21E-07 NO DATA NO DATA NO DATA 3.66E-05 SR-92 - 3.05E-06 NO DATA 1.30E-07 NO DATA- NO DATA NO DATA 7.77E-05 Y-90 l'37E-08 NO DATA 3.69E-10 NO DATA NO DATA NO DATA 1.13E-04 CLINTON-1 3-68 Rev.1-11/85
CPS-ODCM TABLE 3.5-8 (continued)
INGESTION DOSE FACTORS FOR TEEN - (DFL1 ) a (mram per pCi ingested)
LIVER T. BODY THYROID ElQQD( 121((2 0I LLI NUCLIDE AQEE 1.29E.10 NO DATA 4.93E.12 NO DATA NO DATA NO DATA 6.09E.09 Y.91m 2.01E.07 NO DATA 5.39E.09 NO E4TA NO DA'tA NO DATA 8.24E.05 Y.91 1.21E.ie NO DATA 3.50E.11 NO DATA NO DATA NO DATA 3.32E.05 Y.92 3.83E 09 NO DATA 1.05E 10 NO DATA NO DATA NO DATA 1.17E 04
! Y.93 2R 95 4.12E 08 1.30E 08 8.94E.09 NO DATA 1.91E 08 NO DATA 3.00E.05 2.37E 09 4.69E.10 2.16E.10 NO DATA 7.11E 10 NO DATA 1.27E 04 ZR.97 NB.95 8.22E.09 4.56E 09 2.51E 09 NO DATA 4.42E 09 NO DATA 1.95E 05 NO DATA 6.03E.06 1.15E 06 NO DATA 1.38E 05 No DATA 1.08E 05 M0 99 TC /;/m 3.32E.10 9.26E 10 1.20E.08 NO DATA 1.38E-08 5.14E.10 6.08E 07 3.60E.10 5.12E.10 5.03E 09 NO ! SATA 9.26E.09 3.12E 10 8.75E 17 TC.101 2.55E 07 NO DATA 1.09E.07 NO DATA 8.99E 07 NO DATA 2.13E 05 RU-103 2.18E.98 NO l'ATA 8.46E 09 NO DATA 2.75E 07 NO DATA 1.76E 05 Rt' 105 3.92E.06 NO DATA 4.94E 07 NO DATA 7.56E 06 NO DATA 1.88E.04 RU.106- 5.45E.05 AC 110m 2.05E 07 1.94E.07 1.18E 07 NO DATA 3.70E 07 NO DATA 3.83E 06 1.38E.06 5.12E 07 1.07E.06 NO DATA NO DATA 1.13E 05 TE l'"
9.67E 06 3.43E 06 1.15E 06 2.30E 06 3.92E-05 NO DATA 2.41E.05 TE 12's.
1.58E 07 5.60E.08 3.40E 08 1.09E 07 6.40E.07 NO DATA 1.22E 05 TE 127 1.63E.05 6.r o 06 2.58E 06 5.26E 06 6.82E 05 NO DATA 6.12E-05 TE 129m 4.48E.08 1.67E 08 1.09E-08 3.20E 08 1.88E 07 NO DATA 2.45E 07 TE 129 2.44E-06 1.17E 06 9.76E 07 1.76E 06 1.22E 05 NO DATA 9.39E 05 TE.131m 2.79E.08 1.15E 08 8.72E 09 2.15E.08 1.22E.07 NO DATA 2.29E.09 TE 131 TE.13; 3.49E-06 2.21E 06~ 2.08E 06 2.33E 06 2.12E 05 NO DATA 7.00E.05 2.98E 06 1.19E 06 2.43E-04 4.59E.06 NO DATA 2.29E 06 1 130 1.03_E 06 1.62E.06 8.19E 06 4.40E 06 2.39E.03 1.41E 05 NO DATA I.131 5.8bE-06 .
7.30E 07 2.62E 07 2.46E 05 1.15E 06 NO DATA 3.18E 07 I-132 2.79E.07 2.58E 06 I.133 2.01E 06 3.41E 06 1.04E 06 4.76E 04 5.98E 06 NO DATA 3.87E.07 1.39E 07 6.45E 06 6.10E 07 NO DATA 5.10E 09 I 134 1.46E 07 l.
CLINTON-1 3-69 Rev.5-2/89 g~
CPS-ODCM TABLE 3.5-8 (continuedi IllGESTIOli DOSE FACTORS FOR TEEli - (DFL1 )a 4 1
(mrom por pCi ingested)
NUCLIDE ff01{.E LIVER T. BODY THYROID ElDLIC lE!Q GI LLI I 135 6.10E 07 1.57E 06 5.82E 07 1.01E404 2.48E 06 NO DATA 1.74E 06 CS 134 8.37E 05 1.97E 04 9.14E.05 NO DATA 6.26E 05 2.39E 05 2.45E 06 CS 136 8.59E 06 3.38E 05 2.27E 05 NO DATA 1.84E 05 2.90E.06 2.72E.06 CS 137 1.12E 04 1.49E 04 5.19E 05 NO DATA 5.07E 05 1.97E 05 2.12E 06 CS 138 7.76E 08 1.49E 07 7.45E 08 NO DATA 1.10E 07 1.28E 08 6.76E 11 BA 139 1.39E.07 9.78E 11 4.0$E.09 NO DATA 9.22E.11 6.74E 11 1.24E 06 EA 140 2.84E 05 3.48E 08 1.83E 06 NO DATA 1.18E 08 2.34E 08 4.38E.05 BA 141 6.71E 08 5.01E 11 2.24E 09 NO DATA 4.65E-11 3.43E.11 1.43E.13 BA.142 2.99E 08 2.99E.11 1.84E 09 NO DATA 2.53E 11 1.99E 11 9.18E 20 LA 140 3.48E 09 1.71E 09 4.55E.10 NO DATA NO DATA NO DATA 9.82E 05 LA 142 1.79E 10 7.95E-11 1.98E 11 NO DATA NO DATA NO DATA 2.42E 06 CE-141 1.33E 08 8.88E.09 1.02E 09 NO DATA 4.18E 09 NO DATA- 2.54E.05 CE 143 2.35E 09 1.71E.06 1.91E 10 NO DATA 7.67E 10 NO DATA 5.14E 05
) CE 144 6.96E 07 2.88E.07 3.74E 08 NO DATA 1.72E 07 NO DATA 1.75E 04 PR 143 1.31E 08 5.23E 09 6.52E 10 NO DATA 3.04E 09 NO DATA 4.31E 05 PR 144 4.30E 11 1.76E 11 2.18E 12 NO DATA 1.01E-11 NO DATA 4.74E 14 ND 147 9.38E 09 1.02E-08 6.11E.10 NO DATA 5.99E 09 NO DATA 3.68E 05 V-187 1.46E 07 1.19E 07 4.17E 08 NO DATA NO DATA NO DATA 3.22E.05 -
NP 239 1.76E 09 1.66E 10 9.22E.11 NO DATA 5.21E 10 NO DATA 2.67E-05
- 4.06 X 10-06
- Less than 10-24 CLIliTON-1 3-70 Rev.1-11/85
CPS-0DCM TABLE 3.5-9 INGESTION DOSE FACTORS FOR ADULT - (DFLi )a ;
(mrem per pCi ingested)
NUCLIDE 3.QHE LIVER T. BODY TIP(ROID KIDNEY L1!HQ GI LLI H3 NO DATA 1.0$E.07 1.05E 07 1.05E 07 1.05E 07 1.05E 07 1.05E 07 C.14 2.84E 06* 5.68E.07 5.68E 07 5.68E 07 5.68E 07 5.68E 07 5.68E 07 NA.24 1.70E.06 1.70E.06 1.70E 06 1.70E.06 1.70E 06 1.70E 06 1.70E 06 P 32 1.93E 04 '1.20E 05 7.46E.06 No DATA NO DATA NO DATA 2.17E.05 CR 51 NO DATA NO DATA 2.66E-09 1.59E 09 5.86E.10 3.53E.09 6.69E 07 MN+54 No DATA 4.57E 06 8.72E 07 NO DATA 1.36E.06 NO DATA 1.40E 05 MN 56 NO DATA 1.15E.07 2.04E.08 NO DATA 1.46E 07 NO DATA 3.67E.06 FE 55 2.75E.06 1.90E 06 4.43E 07 NO DATA NO DATA 1.06E.06 1.09E 06 FE 59 4.34E.06 1.02E.05 3.91E 06 NO DATA NO DATA 2.85E-06 3.40E 05 CO 58 NO DATA 7.45E.07 1.67E 06 NO DATA NO DATA NO DATA 1,51E 05 CO.60 NO DATA 2.14E 06 4.72E 06 NO. DATA NO DATA NO DATA 4.02E 05 NI 63 1.30E.04 9.01E.06 4.36E.06 NO DATA NO DATA NO DATA 1.88E 06 NI 65 5.28E 07 6.86E 08 3.13E.08 NO DATA NO DATA NO DATA 1.74E 06 )
-CU.64 N0' DATA 8.33E 08 3.91E.08 NO DATA 2.10E 07 NO DATA 7.10E 06
.ZN 65 4.84E.06 1.54E 05 6.96E.06 NO DATA 1.03E.0. NO DATA 9.70E.06 ZN.69 1.03E 08, 1.97E 08 1.37E.09 NO DATA 1.28E 08 NO DATA 2,96E-09 BR.83 NO DATA NO DATA 4.02E.08 NO DATA NO DATA NO DATA 5.79E 08 BR 84 NO DATA. NO DATA 5.21E 08 NO DATA NO DATA NO DATA 4.09E.13 BR 85 NO DATA NO DATA 2.14E.09 NO DATA NO DATA NO DATA LT E 24**
RB 86 NO DATA 2.11E.05 9.83E 06 NO DATA NO DATA' NO DATA 4.16E.06 RB 88 NO DATA. 6.03E.08 3.21E 08 NO DATA NO DATA NO DATA 8.36E.19 RB.89 NO DATA 4.01E.08 2.82E 08 NO DATA NO DATA NO DATA 2,33E 21 SR 89: 3,08E.04 NO DATA 8.84E 06 NO DATA NO DATA NO DATA 4.94E 05 SR 90 7.58E.03 NO DATA 1.86E 03 NO DATA NO DATA NO DATA 2.19E.04
,s.67E 06 2,29E-07 NO DATA NO DATA NO DATA 2 , 7 0 E . O .,
SR 91 .NO DATA SR 92 2.15E-06 NO DATA 9.30E 08 NO DATA NO DATA NO DATA 4.26E-05 Y.90 9.62E.09 NO DATA 2.58E.10 NO DATA NO DATA NO DATA 1.00E 04 CLINTON-11 3-71 Rev 1-11/85
CPS-ODCM TABLE 3.5-9 (continuedt
! IliGESTIOli DOSE FACTORS FOR ADULT - (DFLi ) a (mrom per pCi ingested)
KIDNEY LW.G GI LLI NUCLIDE EF LIVER T. BODY THYROID.
Y 91m 9 M 1> NO DATA 3.52E 12 NO DATA NO DATA NO DATA 2.67E 10 Y 91 1. '4 NO DATA 3.77E 09 NO DATA NO DATA NO DATA 7.76E 05 Y 92 8.% E 10 NO DATA 2.47E 11 110 DATA NO DATA 110 DATA 1.48E 05 Y 93 2.68E 09 NO DATA 7.40E 11 NO DATA 110 DATA NO DATA 8.50E 05 ZR 95 3.04E 08 9.75E 09 6.60E 09 NO DATA 1.53E 08 NO DATA 3.09E 05 ZR 97 1.68E 09 3.39E 10 1.55E 10 NO DATA 5.12E 10 NO DATA 1.0$E 04 NB 95 6.22E 09 3.46E 09 1.86E 09 NO DATA 3.42E-09 NO DATA 2.10E 05 MO 99 NO DATA 4.31E 06 8.20E 07 NO DATA 9.76E 06 'O DATA 9.99E 06 2.47E 10 6.98E 10 8.89E 09 NO DATA 1.06E 08 3.42E 10 4.13E 07 TC 99c TC 101 2.54E-10 3.66E 10 3.59E-09 NO DATA 6.59E 09 1.87E 10 1.10E 21 RU 103 1.85E 07 NO DATA 7.97E 08 NO DATA 7.06E 07 NO DATA 2.16E 05 RU-105 1.54E-08 NO DATA 6.08E 09 NO DATA 1.99E 07 NO DATA 9.42E 06 2.75E 06 NO DATA 3.48E 07 NO DATA 5.31E 06 NO DATA 1.78E 04
) RU 106 2.91E 07 NO DATA 6.04E 05 A0 110m 1.60E-07 1.48E 07 8.79E 08 NO DATA TE 125m 2.68E 06 9.71E 07 3.59E 07 8.06E 07 1.09E 05 NO DATA 1.07E 05 TE 127m 6.77E 06 2.42E 06 8,23E 07 1.73E 06 2.75E 05 NO DATA 2.27E 05 1.10E 07 3.95E 08 2.38E 08 8.15E 08 4 "E 07
- NO DATA 8.68E 06 TE 127 3.95E 06 4.2 E 05 NO DATA 5.79E-05 TE-129m 1.15E 05 4.29E 06 1.82E 06 }
TE-129 3.14E 08 1.18E 08 7.65E 09 2.41E-08 1.32E 07 NO DATA 2.37E 08 TE-131m 1.73E 06 8.46E 07 7,0$E 07 1.34E 06 8.57E-06 NO DATA 8.40E 05 TE-131 1,97E 08 8.23E 09 6.22E 09 1.62E-08 8.63E 08 NO DATA 2.79E 09 TE-132 2.52E 06 1.63E 06 1.53E 06 1.80E 06 1.57E 05 NO DATA 7.71E 05 I 130 7.56E 07 2.23E 06 8.80E 07 1.89E 04 3.48E 06 NO DATA 1.92E-06 1 131 4.16E-06 5.95E 06 3.41E 06 1.95E 03 1.02E 05 NO DATA 1.57E-06 5.43E 07 1,90E 07 1.90E 05 8.65E 07 NO DATA 1.02E-07 I 132 2.03E 07 2.22E 06 I-133 1.42E 06 2.47E 06 7.53E 07 3.63E 04 4.31E 06 NO DATA I 134 1.06E 07 2.88E 07 1.03E 07 4.99E-06 4.58E 07 NO DATA 2.51E 10 CLINTON-1 3-72 Rev.5-2/89
CPS-ODCM TABLE 3.5-9 (continued)
INGESTION DOSE FACTORS FOR ADULT - (DFLi )a (mrem per pci ingested)
$1UCLIDE 101{g LIVER T. BODY TIPIROID KIDNEY QqLQ GI - LI I I 135 4.43E.07 1.16E.06 4.28E 07 7.65E 05 1.86E.06 NO DATA 1.31E.06 CS 134 6.22E 05 1.48E.04 1.21E.04 NO DATA 4.79E.05 1.59E.05 2.59E 06 CS.136 6.51E 06 2.57E 05 1.85E 05 NO DATA 1.43E.05 1.06E 06 2.92E 06 CS 137 7.97E.05 1.09E.04 7.14E.05 NO DATA 3.70E.05 1.23E 05 2.11E 06 CS 138 5.52E 08 1.09E.07 5.40E 08 NO DATA 8.01E 08 7.91E.09 4.65E.13 BA.139 9.70E 08 6.91E 11 2.84E,4' NO DATA 6.46E.11 3.92E.11 1.72E 07
-B4 140 2.03E-05 2.55E 08 1.33E.06 NO DATA 8.67E.09 1.46E 08 4.18E.05 BA 141 4.71E 08 3.56E-11 1.59E 09 NO DATA 3.31E 11 2.02E.11 2.22E.17 BA.142 2.13E.08 2.19E.11 1.34E 09 NO DATA 1.85E.11 1.24E 11 3.00E.26 IA 140 2.50E.09 1.26E.09 3.33E.10 NO DATA NO DATA NO DATA 9.25E.05 LA 142- 1.28E.10 5.82E 11 1.45E-11 NO DATA NO DATA NO DATA 4.25E 07 CE 141 9.36E 09 6.33E 09 7.18E 10 NO DATA 2.94E.09 NO DATA 2.42E 05 CE 143 1.65E 09 1.22E 06 1.35E-10 NO DATA 5.37E.10 NO DATA 4.56E 05 )
CE 144 4.88E.07 2.04E.07 2.62E.08 NO DATA 1.21E 07 NO DATA 1.65E.04 PR 143 9.20E.09 3.69E.09 4.56E.10 NO DATA 2.13E 09 NO DATA 4.03E 05 PR 144 3.01E.11 1.25E 11 1.53E.12 NO DATA 7.05E.12 NO DATA 4.33E.18 ND 147 6.29E 09 7.27E 09 4 35E.10 NO DATA 4.25E-09 NO DATA 3.49E.05 W.187 1.03E.07 8.61E.08 3.01E 08 NO DATA NO DATA NO DATA 2.82E-05 NP.239 1.19E.09 1.17E.10' 6.45W.11 NO DATA 3.65E 10 NO DATA 2.40E 05
- 2.84 X 10-06
- Less than 10-24 CLINTON-1 3-73 Rev.1-11/85
CPS-ODCM TABLE 3.5-10 INPUT PARAMETERS FOR CALCULATING Raij Parerteter Value Table
- Qy (kg/ day) 50 for cow E3 6 for goat E3 Uap (liters'yr) Infant 330 E5
- Child 330 E5
- Teen 400 E5
- Adult 310 E5 Yp (kg/m2 ) 0.7 E 15 Y (kg/m 2) 2.0 E-15 Fm (days / liter) Each stable element for cow E1 Each stable element for goat E2 r (dimensionless) 1.0 for radiciodine E 15 0.2 for particulates E 15 tg (seconds) 1.73 x 105 (2 days) E 15 th (seconds) 7.78 x 106 (90 days) E 15
) f, (dimensionless) 1.0 for cow !WREG 1.0 for goat -0133 Section 5.3.1.3 fp (dimensionless) 1.0 for cow INREG 1.0 for goat 0133 Section 5.3.1.3 .-
- of Regulatory Guide 1.109 unless otherwise stated CLIKTON-1 3-74 Rev.1-11/85 4
.m__ _ _ _ _ _ _ _ . _ _ _ _ _ _ _ _ _ _ _ _ . _ _ _ _ _ _ _ _ . _ . _ _ _ _ _ _ _ _ _ , _ _ _ _ _ _,__ _
CPS-ODCM TABLE 3.9-11 INPUT PARAMETERS FOR CALCULATING Raij Parameter Value Table * ,
Uap (kg/yr) . Infant 0 E5
. Child 41 E.5
. Teen 65 E5 Adult 110 E.5 ,
i Fg (days /kg) Each stable E1 element S. (seconds) 1.73E+06 E 15 (20 days) th (seconds) 7.78E+06 E 15 (90 days)
Yp (kg/m2 ) 0.7 E 15 Y, (kg/m2 ) 2.0 E 15 r (dimensionless) 1.0 for radiciodine E 15
,0.2 for particulates E 15
- Qg (kg/ day) 50 E.3 3
cof Regulatory Guido 1.109 f
CLINTON 3-75 Rev.1-11/85
CPS ~ODCM I l
TABLE 3.g ip V
INPUT PARAMETERS FOR CALCULATING R aij Parameter Value Table
- L Ua (kg/yr) Infant 0 E5 Child 26 E5
- Teen 42 E5 ,
- Adult 64 E5 '
S Ua (kg/yr) - Infant 0 E5 Child 520 E5 Teen 630 E5 Adult 520 E5 ft (dimensionless)- 1.0 E 15 fg (dimensionless). 0.76 E 15 t-(seconds L' 8.6 x 104 (1 day) E 15 ch (seconds) 5.18 x 100 ;60 days) E 15 Yy (kg/m*) 2.0 E 15
)
- of Regulatory Guide-1.109 CLINTON-1 3-76 ReV 1-11/85 s.-e ..,, - - - . . .- , , - - mn --
m n-, ..n.- .y-.--
CPS-ODCM l TABLE 3.5-13 I !
INHAIATION PATHWAY FACTORS - Raij (IN N T)
(mrom/yr per gCi/m3 )
i ORGAth ME LIVER T. BODY THYROID }'MEX IEG GI.LLI fSOTOPE H3 NO DATA 6.47E+02* 6.47E+02* 6.47E+02* 6.47E+02* 6.47E+02 6.47E+02*
C 14 2.65E+04 5.31E+03 5.32E+03 5.31E+03 5.31E+03 5.31E+03 5.31E+03 NA 24 1.06E+04 1.06E+04 1.06E+04 1.06E+04 1.06E+04 1.06E+04 1.06E+04 P 32 2.03E+06 1.12E+05 7.74E+04 NO DATA NO DATA NO DATA 1.61E+04 CR 51 .NO DATA NO DATA 8.95E+01 5.75E+01 1.32E+01 1.28E+04 3.57E+02 MN 54 NO DATA 2.53E+04 4.98E+03 NO DATA 4.98E+03 1.00E+06 7.06E+03 ;
1 MN.56 NO-DATA 1.54E+00 2.21E.01 NO DATA 1.10E;00 1.25E+04 7.17E+04 FE.55 1.97E404 1.17E+04- 3.33E+03 NO DATA NO DATA 8.69E+04 1.09E+03 FE.59 1.36E+04 2.35E+04 9.48E+03 NO DATA NO DATA 1.02E+06 2.48E+04 CO.58 NO DATA 1.22E+03- 1.82E+03 NO DATA NO DATA 7.77E+05 1.11E+04 CO.60 NO DATA 8.02E+03- 11.18E+04 NO DATA NO DATA 4.51E+06 3.19E+04 NI 63 3.39E+05 2.04E+04 1.16E+04 NO DATA NO DATA 2.09E+05 2.42E+03 I
NI.65 2.39E+00' 2.84E.01 1.23E 01 NO DATA NO DATA 8.12E+03 5.01E+04 CU.64 NO DATA 1.88E+00 7.74E.01 NO DATA 3.98E+00 9.30E+03 1.50E+04 ZN 65 1.93E+04 6.26E+04 3.11E+04 N9 DATA 3.25E+04 6.47E+05 5.14E+04 9.67E 02 7.18E.03 NO DATA 4.02E.02 1.47E+03 1.32E+04 ZN.69 5.39F. 02 l NO DATA- 3.81E+02 NO DATA NO DATA NO DATA LT1. 4 E .15 **
BR 83 -NO DATA BR.84 NO DATA NO DATA 4.00E+02 NO DATA NO DATA NO DATA LT1.4E.15 l
l 2.04E+01 NO DATA NO DATA NO DATA LT1.4E.15 BR 85 NO DATA NO DATA 1.90E+05 8.82E+04 NO DATA NO DATA NO DATA 3.04E+03 RB.86 NO DATA 5.57E+02 2.87E+02 NO DATA NO DATA NO DATA 1.39E+02 RB 88 NO DATA-1 l
L 2.06E+02 NO DATA NO DATA NO DATA 6.82E+01 RS 89 NO DATA - 3.21E+02 1.14E+04 NO DATA NO DATA 2.03E+06 6.40E+04 SR.89- 3.98E+05 NO DATA 1.31E+05 SR.90 4.09E+07- NO DATA '2.59E+06 NO DATA NO DATA 1.12E+07 3-77 Rev.5-2/89 CLINTON-1 v-,- ., .,-.w,w,,-..,,,,--
, - , , , , - - - - - - - - - - , -,,,,.,.---,.-...,_...,-..+.y _ , . , . . - w ,,m. ,2-m .
..-r-
CPS-CDCM l FABLE 3.5-U (continued)
IN!!ALATION PATIDIAY FACTORS - Raij (IN N T) ;
3 (mrem /yr per pCi/m )
i ORGA!h IP.HE LIVER T. BODY THYROID KIDNEY J2{G GI LLI JSOTOPE SR 91 9.56E+01 NO DATA 3.46E+00 NO DATA NO DATA 5.26E+04 7.34E+04 SR 92 1.05E+01 NO DATA 3.91E 01 NO DATA NO DATA 2.38E+04 1.40E+05 Y-90 3.29E+03 NO DATA 8.82E+01 NO DATA NO DATA 2.69E+05 1.04E+05 Y-91m 4.07E 01 NO DATA 1.39E 02 NO DATA NO DATA 2.79E+03 2.35E+03 Y 91 5.88E+05 NO DATA 1.57E+04 NO DATA NO DATA 2.45E+06 7.03E+04 Y 92 1.64E+01 NO DATA 4.61E 01 NO DATA NO DATA 2.45E+04 1.27E+05 Y 93 1.50E+02 NO DATA 4.07E+00 NO DATA- NO DATA 7.64E+04 1.67E+05 ER 95 1.15E+05 2.79E+44 2.03E+04 No DATA 3.11E+04 1.75E+06 2.17E+04 i
-IR 97 1.50E+02 2.56E+01 1.17E+01 NO DAi'A 2.59E+01 1.10E+05 1.40E+05
'NB 95 1.57E+u 6.43E+03 3.78E+03 NO DATA 4.72E+03 4.79E+05 1.27E+04 MO 99 NO DATA 1.65E+02 3.23E+01 NO DATA 2.65E+02 1.35E+05 4.87E+04 TC 99m 1.40E 03 2.88E 03 3.72E 02 NO DATA 3.11E 02 8.11E+02 2.03E+03
)TC101 6.51E 05 8.23E 05 8.12E 04 NO DATA 9.79E-04 5.84E+02 8.44E+02 RU-103. 2.02E+03 NO DATA 4 6.79E+02 NO DATA 4.24E+03 5.52E+05 1.61E+04 RU 105 .1.22E+00 NO DATA 4.10E 01 NO DATA 8.99E 01 1.57E+04 4.84E+04 RU-106 8.68E+04 NO DATA 1.09E+04 NO DATA 1;07E+05 1.16E+07 1.64E+05 AG-110m 9.98E+03 7.22E+03 5.00E+03 NO DATA 1.09E+04 3.67E+06 3.30E+04 TE 125m 4.76E+03 1.99E+03 6.58E+02 1.62E+03 NO DATA 4.47E+05 1.29E+04 TE 127m. 1.67E+04 6.90E+03 2.07E+03 4.87E+03 3.75E+04 1.31E+06 2.73E+04 TE 127 2.23E+00 9.53E-01 4.89E 01 1.85E+00 4.86E+00 1.03E+04 2.44E+04 TE 129m 1.41E+04 6.09E+03 2.23E+03 5.47E+03 3.18E+04 1.68E+06 6.90E+04 TE-129 -7.88E 02 3.47E+02 1.88E 02 6.75E 02 1.75E 01 3.00E+03 2.63E+04 TE 131m 1.07E+02 5.50E+01 3.63E+01 8.93E+01 2.65E+02 1.99E+05 1.19E+05 TE-131- 1.74E 02 8.22E 03 5,00E 03 1.58E-02 3.99E 02 2.06E+03 8.22E+03 TE-132 - 72 E+02 -
. 2.37E+02 1.76E+02 2.79E+02 1.03E+03 3.40E+05 4.41E+04 L 130 6.39E+03 1.39E+04- 5.57E+03 1.60E+06 1.53E+04 NO DATA 1.99E+03 1-131 3.79E+04 .4.44E+04 1.96E+04 1.48E+07 5.18E+94 NO DATA 1.06E+03 CLINTON-1 3-78 Rev.5-2/89
- -, . . . . - . - . - - - - , . _ . . . - . - . - . - _ . - - . . . - . ~ . . . - . . . - - - - - -
CPS ODCM TABLE 3.5-13 (continuedL INHALATION PATINAY FACTORS - Raij (INFANT)
(mrem /yr per pCi/m3)
ORGAN: jlM.E LIVER T. BODY THYROID KIDNEY ]dl{Q GI-LLI ISOTOPE I 132 1.69E+03 3.54E+03 1.26E+03 1.69E+05 3.95E+03 No DATA 1.90E+03 1 133 1.32E+04 1.92E+04 5.60E+03 3.56E+06 2.24E+04 NO DATA 2.16E+03 I 134 9.21E+02 1.88E+03 6.65E+02 4.45E+04 2.09E+03 NO DATA 1.29E+03 1 135 3.86E+03 7.60E+03 2.77E+03 6.96E+05 8,47E+03 NO DATA 1.83E+03 CS 134 3.96E+05 7.03E+05 7.45E+04 NO DATA 1.90E+05 7.97E+04 1.33E+03 CS 136 4.83E+04 1.35E+05 5.29E+04 NO DATA 5.64E+04 1.18E+04 1.43E+03 CS 137 5.49E+05 6.12E+05 4.55E+04 NO DATA 1.72E+05 7.13E+04 1.33E+03 CS 133 5.05E+02 7.81E+02 3.98E+02 NO DATA 4.10E+02 6.54E+01 8.76E+02 BA 139 1.48E+00 9,84E 04 4.30E 02 NO DATA 5.92E 04 - 5.95E+03 5.10E+04 BA 140 5.60E+04 5.60E+01 2.90E+03 NO DATA 1.34E+01 1.60E+06 3.84E+04 BA 141 1.57E 01 1.08E 04 4.97E 03 NO DATA 6.50E 05 2.97E+03 4.75E+03 3.98E 02 3.30E 05 1.96E 03 NO DATA 1.90E 05 1.55E+03 6.93E+02 B,A 142 i
LA 140 5.0$E+02 2.00E+02 5.15E+01 NO DATA NO DATA 1.68E+05 8.48E+04
-!A 142 1.03E+00 3.77E 01. 9.04E 02 NO DATA NO DATA 8.22E+03 5.95E+04 CE 141 2.77E+04 1.67E+04 1.99E+03 NO DATA 5.25E+03 5.17E+05 2.16E+04 CE 143 2.93E+02 1.93E+02' 2.21E+01 NO DATA 5.64E+01 1.16E+05 4.97E+04 CE 144 3.19E+06 1.21E+06 1.76E+05 NO DATA 5.38E+05 9.84E+06 1.48E+05 PR 143 1.40E+04 5.24E+03 6.99E+02 NO DATA 1.97E+03 4.33E+05 3.72E+04
- m. .
PR 144 4.79E.02 1.85E 02 2.41E 03 NO DATA 6.72E 03 1.61E+03 4.28E+03 ND-147 7.94E43 8.13E+03 5.00E+02 NO DATA 3.15E+03 3.22E+05 3.12E+04 W 187 1.30E+01 9.02E+00- 3.12E+00 NO DATA NO DATA 3.96E+04 3.56E+04 l-NP 239 3.71E+02 3.32E+01 1.88E+01 NO DATA 6.62E+01 5.95E+04 2.49E+04
- 6.47 x 10 2
- Less than 1.40'x 10-15 l
i I
)
CLINTON-1 3-79 Rev.5-2/89 v :
j t
CPS-ODCM TABLE 3. S-M INHALATION PATHWAY FACTORS - R aij (CHILD)
(mram/yr per NCi/m 3)
ORGAN:. AQEZ LIVER T. BODY THYROID KIDNEY Li&{fi GI-LLI HQTOPE 1
H.3 NO DATA 1.12E+03* 1.12E+03 1.12E+03 1.12E+03 1.12E+03 1.12E+03 i C 14 3.58E+04 6.73E+03 6.73E+03 6.73E+03 6.73E+03 6.73E+03 6.73E+03 l NA.24 1.61E+04 1.61E+04 1.61E+04 1.61E+04 1.61E+04 1.61E+04 1.61E+04 l l
P 32 2.60E+06 1.14E+05 9.87E+04 NO DATA NO DATA NO DATA 4.21E+04 ,
CR 51 NO DATA NO DATA 1.54E+02 8.54E+01 2.43E+01 1.70E+04 1.08E+03 MN 54 NO DATA 4.29E+04 9.51E+03 NO DATA 1.00E+04 1.58E+06 2.29E+04 MN.56- NO DATA 1.66E+00 3.12E 01 NO DATA 1.67E+00 1.31E+04 1.23E+05 FE.55 ' 4.74E+04 2.52E+04 7.77E+03 NO DATA NO DATA 1.11E+05 2.57Et03 FE 59 2.07E+04 3.34E+04 1.67E+04 NO DATA NO DATA 1.27E+06 7.07E+04 CO.58 NO DATA 1.77E+03 3.16E+03 NO DATA NO DATA 1.11E+06 3.44E+04 C0 60 NO DATA 1.31E+04 2.26E+04 NO DATA NO DATA 7.07E+06 9.62E+04 NI 63 8.21E+05 4.63E+04 2.80E+04 NO DATA NO DATA 2.73E+05- 6.33E+03 NI 65 2.99E+00' 2.96E 01 1.64E 01 NO DATA NO DATA 8.18E+03 8.40E+04 CU.64 NO DATA 1.99E+00 1.07E+00 NO DATA 6.03E+00 9.58E+03 3.67E+04
'ZN 65 4.26E+04 1.13E+05 7.03E+04 NO DATA 7.14E+04 9.95E+05 1.63E+04 ZN.69 6.70E 02 9.66E 02 8.92E.03 NO DATA 5.SSE.02 1.42E+03 1.02E+04 BR 83 NO DATA NO DATA 4.74E+02 NO DATA NO DATA NO DATA LT3.70E 15** -
BR 84 NO DATA NO DATA 5.48E+02 NO DATA NO DATA NO DATA LT3.70E 15 BR 85 NO DATA NO DATA 2.53E+01 NO DATA NO DATA NO DATA LT3.70E.13 RB.86 NO DATA 1.98E+05 1.14E+05 NO DATA NO DATA NO DATA 7.99E+03 RB 88 NO DATA 5.62E+02 3.66E+02 NO DATA NO DATA NO DATA 1.72E+01 RE.89 NO DATA 3.45E+02 2.89E+02 NO DATA NO DATA NO DATA- 1.89E+00 SR.89- 5.99E+05 NO DATA- 1.72E+04 NO DATA NO DATA 2.16E+06 1.67E+05 SR 90 - 1.01E+08 NO DATA 6.44E+06 NO DATA NO DATA 1.48E+07 3.43E+05 SR 91. 1.21E+02 NO DATA 4.59E+00 NO DATA NO DATA 5.33E+04 1.74E+05 SR 92- -
1.31E+01 NO DATA 5.25E 01 NO DATA NO DATA 2.40E+04- 2,42E+05 Y.90 4.11E+03 NO DATA 1.11E+02 NO DATA NO DATA 2.62E+05 2.66E+05
-t l
CLINTON-1 3-80 Rev.5-2/89 p: e
- . . . . . - ,,m.- ..m m .._r,. .%-.. _.
m.._...,. .,,-._..-._.,,.y..,._ ,m _ , , , , _ . . _ . , = -,,.-_.-.._,...c , . _ . . , _ . . - . , , _ . ~ , , m,. m , _
CPS-CDCM TABLE 3.5-14 (continued)
I!UIALATION PATHWAY FACTORS - Raij (CH M (mrem /yr per #C1/m3 ) l l
T. BODY THYROID KIDNEY 13!q CI.LLI DRGAN . 1Q.11E LIVER ISOTOPE l 1.84E.02 NO DATA NO DATA 2.81E+03 1.72E+03 Y.91m 5.07E 01 NO DATA 2.44E+04 NO DATA NO DATA 2.63E+06 1.84E+0?
Y.91 9.14E+05 NO DATA 5.81E.01 NO DATA NO DATA 2.39E+04 2.39E+05 Y.92 2.04E+01 NO DATA 5.11E400 NO DATA NO DATA 7.44E+04 3.89E+05 Y.93 1.86E402 NO DATA 4.18904 3.70E+04 NO DATA 5.96E+04 2.23E+06 6.11E+04 l ER 95 1.90E+05 2.72E+01 1.60E+01 NO DATA 3.89E+01 1.13E+05 3.51E+05 j ZR-97 1.88E+02 9.18E+03 6.55E+03 NO DATA 8.62E+03 6.14E+05 3.70E+04 NB 95 2.35E+04 1.72E+02 4.26E+01 NO DATA 3.92E+02 1.35E+05 1.27E+05 i M0 99 MO DATA 3.48E.03 5.77E 02 NO DATA 5.07E.02 9.51E+02 4.81E+03 TC-99m 1.78E 03 8.51E 05 1.08E 03 NO DATA 1.45E.03 5.84E+02 1.63E+01 TC.101 8.10E.05 2.79E+03 NO DATA 1.07E+03 NO DATA 7.03E+03 6.62E+05 4.48E+04 RU.103 1.53E+00 NO DATA 5.55E 01 NO DATA 1.34E&OO 1.59E+04 9.95E+04 ,
RU.105 i .I 1.36E&05 NO DATA 1.69E+04 NO DATA 1.84E+05 1.43E+07 4.29E+05 RU 106 1.14E+04 9.14E+03 NO DATA 2.12E+04 5.48E+06 1.00E+05 A0 110m 1.69E+04 2.33E+03 9.14E+02 1.92E+03 NO DATA 4.77E+05 3.38E+04 TE.125m 6.73E+03 8.55E+03 3.02E+03 6.07E+03 6.36E+04 1.48E+06 7.14E+04 TE.127m 2.49E+04 2.77E+00 9.51E 01 6.11E.01 1.96E+00 7.07E+00 1.00E+04 5.62E+C4 TE.127-1.92E+04 6.85E+03 3.04E+03 6.33E+C 5.03E+04 1.76E+06 1.82E+05 TE.129m 9.77E 02 3.50E 02 2.38E 02 7.14E.02 2.57E.01 2.93E+03 2.55E+04 TE 129 1.34E+02 5.92E+01 5.07E+01 9.77E+01 4.00E+02 2.06E+05 3.08E+05
'5E.131m 2.17E.02 8.44E.03 6.59E 03 1,70E.02 5.88E.02 2.05E+03 1.33E+03 TE.131 TE.132 4.81E+02 2.72E+02 2.63E+02 -3.17E+02 1.77E+03 3.77E+05 1.38E+05 1.64E+04 8.44E+03 1.85E+06 2.45E+04 NO DATA 5.11E+03 1 130 8.18E+03 1 131 -4.81E+04 4,81E+04 2.73E+04 1.62E+07 7.88E+04 NO DATA 2.84E+03 i
2.12E+t3 4.07Et03 1.88E+03 1.94E+05 6.25E+03 NO DATA 3.20E+03 1 132 1 133 1.66E+04 2.03E+04 7.70E+03 3.85E+06 3.38E+04 NO DATA 5.48E+03 I-134 1.17E+03 2.16E+03 9.95E+02 5.07E+04 3,30E+03 50 DATA 9.54Et02 4 CLINTON 3-81 Rev.5-2/89
~+ -_ r. v vy,. ,, ._e-., . - . - .,y.. , . , - , . - . . . - , . , ...~.y.,.. _ , - . , , ..~..-w,.-- ,m.--m y. , , . . . . . . , , , , -
i.---.
CPS-ODCM TABLE 3.5-14 (continued)
INHALATION PATHWAY FACTORS - Raij- (CHILD)
(mrem /yr per pCi/m 3)
ORGAlh EBI LIVER T. BODY TlfYROID KIDNEY 14EQ CI LLI ISOTOPE I 135 4.92E+03 8.73E+03 4.14E+03 7.92E+05 1.34E+04 NO DATA 4.44E+03 CS 134 6."1E+05 1.01E+06 2.25E+05 NO DATA 3.30E+05 1.21E+05 3.85E+03 CS 136 6.51E+04 1.71E+05 1.16E405 NO DATA 9.55E+04 1.45E+04 4.18E+03 CS 137 9.70E+05 8.25E+05 1.28E+05 NO DATA 2.82E+05 1.04E+05 3.62E+03 CS 138 6.33E+02 8.40E+02 5.55E+02 NO DATA 6.22E+02 6.81E+01 2.70E+02 DA 139 1.84E+00 9.84E 04 5.37E 02 NO DATA 8.62E 04 5.77E+03 5.77E+04 BA 140 7.40E+04 6.48E+01 4.33E+03 NO DATA 2.11E+01 1.74E+06 1.02E+05 BA-141 1.96E 01 1.09E 04 6.36E 03 NO DATA 9.47E 05 2.92E+03 2.75E+02 BA 142 5.00E 02 3.60E 05 2.79E 03 NO DATA 2.91E 05 1.64E+03 2.74E+00 LA 140 6.44E+02 2.25EcJ2 7. 55E401 NO DATA NO DATA 1.83E+05 2.26E+05 LA-142 . 1.30E+00 4.11E 01 1.29E 01 NO DATA NO DATA 8.70E+03 7.59E+04 CE 141 3.92E+04 1.95E+05 2 90E+03 NO DATA 8.55E+03 5.44E+05 5.66E+04 CE 143 J.66E+02 1.99E+02 2.87E+01 NO DATA 8.36E+01 1.15E+05 1.27E+05 CE 144 6.77E+06 2.12E+06 3.61E+05 NO TATA 1.17E+06 1.20E+07 3.89E+05
?R 143 1.85E+04 5.55E+03 9.14E+02 NO DATA 3.00E+03 4.33E+05 9.73E+04 PR 144 5.96E 02 1.85E-02 3.00E 03 NO DATA 9.77E 03 1.57E+03 1.97E+02 ND 147 1.08E+04 8.73E+03 6.81E+02 NO DATA 4.81E+03 3.28E+05 8.21E+04 W-187 1.63E+01 9.66E+00 4.33E+00 NO DATA NO DATA 4.11E+04 9.10E+04 NP 239 4.66E+02 3.34E+01 2.35E+01 NO DATA 9.73E+01 5.81E+04 6.40E+04
- 1.12 x 10 3
- .Less than-3 70 x 10-15
- CLINTON-1 3-82 Rev.5-2/89 e-- * ,e------ -- * ,e.- -- - ~w---
CPS-0DCM TABLE 3.5- 4 INHALATION PATHWAY FACTORS - Raij (TEEN)
(mrem /yr per pC1/m3 )
T. BODY THYROID KIDNEY LIEG GI LLI ORGAN
- AQEE LIVER ISOTOPE 1.27E+03* 1.27E+03 1.27E+03 1.27E+03 1.27E+03 1.27E+03 11 3 NO DATA 4.87E+03 4. 873+03 ' 4. 87E+03 4.87E+03 4.87E+03 4.87E+03 C 14 2.60E+04 1.38E+04 1.38E+04 1.38E+04 1.38E+04 1.38E+04 1.38E+04 NA 24 1.38E+04 1.10E+05 7.16E+04 NO DATA NO DATA NO DATA 9.28E+04 P 32 1.89E+06 1.35E+02 7.50E+01 3.07E+01 2.10E+04 3.00E+03 CR 51 NO DATA NO DATA 5.11E+04 8.40E+03 NO DATA 1.27E+04 1.98E+06 6.68E+04 MN 54 NO DATA 2.52E-01 NO DATA 1.79E+00 1.52E+04 5.74E+04 MN 56 NO DATA 1.70E+00 2.38E+04 5.54E+03 NO DATA NO DATA 1.24E+0$ 6.39E+03 FE 55 3.34E+04
- 3.70E+04 1.43E+04 NO DATA NO DATA 1.53E+06 1.78E+05 FE 59 1.59E+04 2.07E+03 2.78E+03 NO DATA NO DATA 1.34E+06 9.52E+04 CO 58 NO DATA 1.51E+04 1.98E+04 NO DATA NO DATA 8.72E+06 2.59E+05 Co 60 NO DATA 1.42E+04 4.34E+04 1.98E+04 NO DATA NO DATA 3.07E+05 NI 63 5.80E+05 I
1.27E 01 NO DATA NO DATA 9.36E+03 3.67E+04 NI 65 2.18E+00 2.93E 01 2.03E400 8.48E 01 NO DATA 6.41E+00 1.11E+04 6.14E+04 CU 64 NO DATA 1.34E+05 6.24E+04 NO DATA 8.64E+04 1.24E+06 4.66E+04 ZN 65 3.86E+04 9.20E 02 6.46E-03 NO DATA 6.02E 02 1.58E+03 2.85E+02 ZN 69 4.83E 02 LTSE 15**
NO DATA 3.44E+02 NO DATA NO DATA NO DATA BR 83 NO DATA NO DATA 4.33E+02 NO DATA NO DATA NO DATA LT8E 15 BR 84 NO DATA NO DATA 1.83E+01 NO DATA NO DATA NO DATA LT8E-15 BR 85 NO DATA 1.90E+05 8.40E+04 NO DATA NO DATA NO DATA 1.77E+04-RB 86 NO DATA 5.46E+02 2,72E+02 NO DATA NO DATA NO DATA 2.92E 05 RB 88 NO DATA 3.52E+02 2.33E+02 NO DATA NO DATA NO DATA 3.38E 07 RB 89 NO DATA 1.25E+04 NO DATA NO DATA 2.42E+06 3.71E+05 SR 89 4.34E+05 NO DATA 7.65E+05 NO DATA 6.68E+06 NO DATA NO DATA 1.65E+07 SR 90 1.08E+08 3.51E+00 NO DATA NO DATA 6,07E+04 2.59E+05 SR 91 8.80E+01 NO DATA 4.06E 01 NO DATA NO DATA 2.74E+04 1.1?E+05 SR 92 9.52E+00 NO DATA 5.59E+05 2,98E+03 NO DATA 8.00E+01 NO DATA NO DATA 2.93E+05 Y 90 CLINTON-1 3-83 Rev.5-2/89 L-
CPS-ODCM TABLE-3.5-15 (coatinued)
' INHALATION PATHWAY FACTORS - Rfij (TEEN) t (mrem /yr per #Ci/m3)
ORCAfD LQHE LIVER T. BODY THYROID MIDNE*Y IElG GI LLI ISOTOPE Y.91m 3.70E.01 NO DATA 1.42E.02 NO DATA NO DATA 3.20E+03 3.02E+01 Y.91 6.61E+05 NO DATA 1.77E+04 NO DATA NO DATA 2.94E+06 4.09E+05 Y.92 1.47E+01 NO DATA 4.29E.01 NO DATA NO DATA 2.68E+04 1.65E+05 Y.93 1.35E+02 NO DATA 3.72E+00 NO DATA NO DATA 8.32E+04 5.79E+05 ZR.95 1.46E+05 4.58E+04 3.15E+04 NO DATA 6.74E+04 2.69E+06 1.49E+05 ZR-97 1.38E+02 2.72E+01 1.26E+01 NO DATA 4.12E+01 1.30E+05 6.30E+05 NB 95 1.86E+04 1.03E+04 5.66E+03 NO DATA 1.00E+04 7.51E+05 9.68E+04 M0 99 NO DATA 1.69E+02 3.22E+01 NO DATA 4.11E+02 1.54E+05 2.69E+05 TC 99m 1.38E.03 3.86E.03 4.99E 02 NO DATA 5.76E.02 1.15E+03 6.13E+03 TC.101 5.92E 05 8.40E.05 8.24E.04 NO DATA 1.52E 03 6.67E+02 8.72E.07 RU.103 2.10E+03 NO DATA 8.96E+02 NO DATA 7.43E+03 7.83E+05 1.09E+05 RU.105 1.12E+00 NO DATA 4.34E.01 NO DATA 1.41E+00 1.82E+04 9.04E+04
)
RU.106 9.84E+04 NO DATA 1.24E+04 NO DATA 1.90E+05 1.61E+07 9.60E+05 AG 110m 1.38E+04 1.31E+04 7.99E+03 NO DATA 2.50E+04 6.75E+06 2.73E+05 TE.125m 4.88E+03 2.24E+03 -6.67E+02 1.40E+03 NO DATA 5.36E+05 7.50E+04 TE.127m 1.80E+04 8.16E+03 2.18E+03 4.38E+03 6.54E+04 1.66E+06 1.59E+05 TE.127 2.01E+00 9.12E 01 4.42E.01 1.42E+00 7.2BE+00 1.12E+04 8.08E+04 TE.129m 1.39E+04 6.58E+03 2.25E+03 4.58E+03 5.19E+04 1.98E+06 4.05E+05 TE.129 7.10E.02 3.38E 02 1.76E 02 5.18E 02- 2.66E.01 3.30E+03 1.62E+03 TE.131m 9.84E+01 6.01E+01 4.02E+01 7.25E+01 4.39E+02 2.38E+05 6.21E+05 TE.131 1.58E.02 8.32E 03 5.04E.03 1.24E.02 6.18E.02 2.34E+03 1.51E+01 TE.132 3 '. 60 E+02 2.90E+02 2.19E+02 2.46E+02 1.95E+03 4.49E+05 4.63E+05 I.130 6.24E+03 1.78E+04 7.17E+03 1.49E+06 2.75E+04 NO DATA 9.12E+03 I.131 3.54E+04 4.91E+04 2.64E+04 1.46E+07' 8.40E+04 NO DATA 6.49E+03 I 132 1.59E+03 -4.38E+03 1.58E+03 1.$1E+05 6.92E+03 NO DATA 1.27E+03 I.133 1.22E+04 2.05E+04 6.22E+03 2.92E+06 3.59E+04 NO DATA 1.03E+04 I.134 2.04E+01 8.88E+02 2.32E+03 8.40E+02 3.95E+04 3.66E+03 NO DATA L
-CLINTON-1 3-84 Rev.5-2/89
i CPS-ODCM TABLE 3.5-15 (cont inuqsi).
INHALATION PATHWAY FACTORS - Raij (TEEN)
(mrem /yr per pCi/m3 )
ORCANt }Q1{g LIVER T. BODY THYROID KIDNEY LlR{.G GI LL 11QTOPE .
3.70E+03 9.44E+03 3.49E+03 6.21E+05 1.49E+04 NO DATA 6.95E+03 )
1 135 5.02E+05' 1.12E+06 5.49E+05 N0' DATA 3.75E+05 1.46E+05 9.76E+03 CS 134 CS-136 5.15E+34 1.94E+05 1.37E+05 NO DATA 1.10E+05 1.78E+04 1.09E+04 !
I 6.70E+05 8.48E+05 3.11E+05 NO DATA 3.04E+05 1.21E+05 8.48E+03 !
CS 137 CS-138 4.66E+02 8.56E+02 4.46E+02 NO DATA 6.6.~ &O2 7.87E+01 2.70E 01 1.34E+40 9.44E 04 3.90E 02 NO DATA 8.88E 04 6.46E+03 6.45E+03 BA 139 .
BA-140 5.47E+04 6.70E+01' 3.52E+03 NO DATA 2.28E+01 2.03E+06 2.29E+05 BA-141 1.42E 01 1.06E 04 4.74E 03 NO DATA 9.84E 05 3.29E+03 7.46E 04 BA v.7 - 3.70E 02 3.70E-05 2.27E 03 NO DATA 3.14E 05 1.91E+03 4.79E 10 LA 140 4.79E+02 2.36E+02 6.26E+01 NO DATA NO DATA 2.14E+05 4.87E+05 1A-142 9.60E 01 4.25E 01 1.06E 01 NO DATA NO DATA 1.02E+04 1.20E+04 CE 141 2.84E+04 1.90E+04 2.17E+03 NO DATA 8.88E+03 6.14E+05 1.26E+05
}
2.66E+02 1.94E+02 2.16E+01 NO DATA 8.64E+01 1.30E+05 2.55E+05 CE 143 4.89E+06 2.02E+06 2.62E+05 NO DATA 1.21E+06 1.34E+07 8.64E+05 CE 144 1.34E+04 5.31E+03 6.62E+02 NO DATA 3.09E+03 4.83E+05 2.14E+05 PR 143 4.30E 02 1.76E 02 2.18E 03 NO DATA 1.01E 02 1.75E+03 2.35E 04 PR 144 1.82E+05 ND 147- 7.86E+03 8.56E+03 5.13E+02 NO DATA 5.02E+03 3.72E+05 9.76E+00 3.43E+00 NO DATA NO DATA 4.74E+04 1.77E+05 ,
V 187 1,20E+01 l
3.19E+01 1.77E+01 NO DATA 3.00E+02 6.49E+04 1.32E+05 NP 239 ' 3.38E+02
- 1.27 x 10 3
- Less tht.a 8.00 x 10-15 CLINTON-1 3-85 Rev.5-2/89 em.v.~,i v
-* e -w,-v--< v -s-w,---w w w -- w w, v. --w----yw-e-s-ww-weg- y g
CPS-ODCM TABLE 3.5-16 :
INHALATION PATHWAY FACTORS - Raij (ADULT)
(mrem /yr per , 3/m 3) L ORGAN: jlgE LIVER T. BODY THYROID MIDNEY L1$G CI-LLI ;
ISOTOPE H3 NO DATA 1.26E+03* 1.26E+03 1.26E+03 1.26E+03 1.26E+03 1.26E+03 C-14 1.82E+04 3.41E+03 3.41E+03 3.41E+03 3.41E+03 3.41E+03 3.41E+03 NA 24 1.02E+04 1.02E+04 1.02E+04 1.02E+04 1.02E+04 1.02E+04 1.02E+04 P 32 1.32E+06 7.71E+04 5.01E+04 NO DATA NO DATA NO DATA 8.64E+04 CR 51 NO DATA NO DATA 1.00EM2 5.95E+01 2.28E+01 1.44E+04 3.32E+03 MN 54 NO DATA 3.96E+04 6.30E+03 NO DATA 9.84E+03 1.40E+06 7.74E+04 MN 56 NO DATA 1.24E+00 1.83E 01 NO DATA 1.30E+00 9.44E+03 2.02E+04 FE 55 2.46E+04 1.70E+04 3.94EM3 NO DATA NO DATA 7.21E+04 6.03E+03 FE 59 1.18E+04 2.78E+04 1.06E+04 NO-DATA NO DATA 1.02E+06 1.80E+05 Co 58 NO DATA 1.58E+03 2.07E+03 NO DATA NO DATA 9.28E+05 1.06E+05 -
CO 60 NO DATA 1.15E+04 1.48E+04 NO DATA NO DATA 5.97E+06 2.85E+05 NI 63 4.32E+05 3.14E+04 1.45E+04 NO DATA NO DATA 1.78E+05 1.34E+04
)
NI-65 1.54E+00 2.10E 01 9.12E 02 NO DATA NO DATA 5.60E+03 1.23E+04 CU 64 NO DATA 1.46E+00 6.15E 01 NO DATA 4.62E+00 6.78E+03 4.90E+04 2N-65 3.24E+04 1.03E+05 4.66E+04 NO DATA 6.90E+04 8.64E+05 5.34E+04 ZN 69 3.38-02 6.51E 02 4.52E 03 NO DATA 4.22E 02 9.20E+02 1.63E+01 BR 83 NO DATA NO DATA 2.41E+02 NO DATA NO DATA NO DATA 2.32E+02 BR 84 NO DATA NO DATA 3.13E+02 NO DATA NO DATA NO DATA 1.64E 03 BR 85 ho DATA NO DATA 1.28E+01 NO DATA NO DATA NO DATA LT8E.15**
RB-86 NO DATA .1.35E+05 5.90E+04 NO DATA NO DATA NO DATA 1.66E+04 R3 88 NO DATA 3.87E+02 1.93E+02 NO DATA NO DATA NO DATA 3.34E 09 RB 89 NO DATA 2.56E+02 1.70E+02 NO DATA NO DATA NO DATA 9.28E 12 SR 89 3.04E+05 NO DATA 8.72E+03 NO DATA NO DATA 1.40E+06 3.50E+05 SR 90- 9.92E+07 NO DATA 6.10E+06 NO DATA NO DATA 9.60E+06 7.22E+05 SR 91 6.19E+01 NO DATA 2.50E+00 NO DATA NO DATA 3.65E+04 1.91E+05 SR 92 6.74E+00 . NO DATA 2.91E-01 NO DATA NO DATA 1.65E+04 4.30E+04 Y 90 2.09E+03 NO DATA 5.61E+01 NO DATA NO DATA 1.70E+05 5.06E+05
-CLINTON-1 3-86 Rev.5-2/89 p w- -,,we ...-,-,y-.7,, -
, ._ - - . - -_ . _ . _ . - . . . . .. - - - -- - - .. - .~ ~._.
CPS-CDCM TABLE 3.5-16 (continued).
IN11ALATION PATliWAY FACTORS - Raij (ADULT)
(mren/yr per #C1/m3 ) ;
r T. BODY THYROID KIDNEY MEQ CI.LLI ORGANr RQ]iE LIVER TsotoPr 1.02E 02 NO DATA NO DATA 1.92E+03 l'.33E+00 Y-91m 2.61E.01 NO DATA 3.85E+05 NO DATA 1.24E+04 NO DATA NO DATA 1.70E+06 T-91 4.62E+05 7.35E+04 1.03E+01 NO DATA 3.02E+01 NO DATA NO DATA 1.57E+04 Y.92 i 2.(1E+00 NO DATA NO DATA 4.85E+04 4.22E+05 Y-93 ~9.44E+01: NO DATA 2.33E+04 NO DATA 5.42E+04 1. 77 E+06 1.50E+05 21-95 1.07E+05 3.44E+04 5,23E+05 1.96E+01 9. 04E+00 NO DATA- 2.97E+01 7.87E+04 ZR-97' 9.68E+01 4.21E+03 NO DATA 7.74E+03 5.05E+05 1.04E+05 NSW955 1.41E+04 7.82E+03 2.30E+01 NO DATA 2.91E+02 9.12E+04 2.48E+05 r M0a 99- NO DATA- 1.21E+02 2.91E.03 3.70E 02 NO DATA 4.42E.02 7.64E+02 4 .16 E+03-TC 99m 1.03E.03 i 6.02E 05 5.90E 04 NO DATA 1.08E.03 3.99E+02 1.09E.11 l TC-101 4.18E.05 1.10E+05 NO DATA 6.58E+02 NO DATA 5.83E+03 5.05E+05 RU 103 1.53E+03 4.82E+04 3.11E 01 NO DATA 1.02E+00 1.10E+04 RU-IOS 7.90E.01 NO DATA
):
8.72E+03 NO DATA 1.34E+05 9.36E+06 9.12E+05
-RU 106 6.91E+04' - NO DATA 3.02E+05 1.00E+04 5.94E+03 NO DATA 1.97E+04 4.63E+06 AG-110m- 1.08E+04 3.14E+05 7.06E+04 1.58E+03 4.67E+02 1.05E+03 1.24E+04 TE 125m 3.42E+03 '
3.29E+03 4.58E+04 9.60E+05 1.50E+05 TE'127m 1.26F+04 5.77E+03- 1.57E+03 1.06E+00 5.10E+00 6.51E+03 5.74E+04 TE 127 1.-40E+00 6.42E-01 3.10E 01 3.44 E+03 3.66E+04 1.16E+06 3.83E+05 TE-I29m 9.76E+03 4.67E+03 1.58E+03 l
3.90E 02 1.87E 01 1.94E+03 1.57E+02 IE-129 ~4.98E 02 2.39E.02 1.24E.02 5.50E+01 3.09E+02 1.46E+05 5.56E+05-TE.131m 6.99E+01- 4.36E+01 2.90E+01 9.36E 03 4.37E-02 1.39E+03 1.84E+01 TE-131 - 1.11E 02 - 5.95E 03 3.59E-03
(. 2.88E+05 5.10E+05
' 2.15E+02 1.62E+02 1.90E+02 1.46E+03 TE 132 2.60E+02 NO DATA 7.69E+03
-1.34E+04 5.28E+03 1.14E+06 2.09E+04 I-00, - 4.58E+03 NO DATA 6.28E+03 3,58E+04 2.05E+04 1.19E+07 6.13E+04 J' Z- D 3L 2.52E+04 1 1.14E+05 5.18E+03 NO DATA 4.06E+02 1-132 1.16E+03 3.26E+03 1.16E+03 2.15E+06 2.58E+04 NO DATA 8.88E+03 1-133 8.64E+03 1.48E+04 4.52E+03 2.98E+04 2.75E+03 NO DATA 1.01E+00 I-134 6.44E+02 1.73E+03 6.15E+02 3-87 Rev.5-2/89 CIJNTON-1
---...i,__.--. ...-6,.,
, ,w.,.-n , , , . . , , , , , , - - . , ,,e , ~ - , -_,,..,,-~.,--,-,.,-,co-
, ,. n --- ,. . .
CPS-ODCM TABLE 3.C3-16 (continued) !
INHALATION PATHWAY FACTORS - R aij (ADULT)
(mrem /yr per pCi/m 3)
ORGAN! 1Q15 LlYEE T. BODY THYR 01D KIDNEY M GI LLI ISOTOPE I 135 2.68E+03 6.98E+03 2.57E+03 4.48E+05 1.11E+04 NO DATA 5.25E+03 CS 134 3.73E+05 8.48E+05 7.28E+05 NO DATA 2.87E+05 9.76E+04 1.04E+04 CS.136 3.90E+04 1.46E+05 1.10E+05 NO DATA 8.56E+04 1.20E+04 1.17E+04 l l
CS.137 4.78E+05 6.21E+05 4.28E+05 NO DATA 2.22E+05 7.52E+04 8.40E+03 CS 138 3.31E+02 6.21E+02 3.24E+02 NO DATA 4.80E+02 ~4.86E+01 1.86E.03 BA 139 9.36E 01 6.66E 04 2.74E 02 NO DATA 6.22E.04 3.76E+03 8.96E+02 BA.140 3.90E+04 4.90E+01 2.57E+03 NO DATA 1.67E+01 1.27E+06 2.18E+05 BA 141 1.00E 01 7.53E 05 3.36E.03 NO DATA 7.00E 05 1.94E+03 1.16E.07 BA.142 2.63E 02 2.70E 05 1.66E 03 NO DATA 2.29E 05 1.19E+03 1.57E 16 IA 140 3.44E+02 1.74E+02 4.58E+01 NO DATA NO DATA 1.36E+05 4.58E+05 IA 142 6.83E.01 3.10E.01 7.72E 02 NO DATA NO DATA 6.33E+03 2.11E+03 CE.141 1.99E+04 1.35E+04 1.53E+03 NO DATA 6.26E+03 3.62E+05 1.20E+05 CE.143 1.86E+02 1.38E+02 1.53E+01 NO DATA 6.08E+01 7.98E+04 2.26E+05 CE.144 3.43E+06 1.43E+06 1.84E+05 NO DATA 8.48E+05 7.78E+06 8.16E+05 PR 143 9.36E+03 3.75E+03 4. 64E4 02 NO DATA 2.16E+03 2.81E+05 2.00E+05 PR 144 3.01E-02 1.25E 02 1.53E.03 NO DATA 7.0$E 03 1.02E+03 2.15E.08 ND 147 5.27E+03 6.10E+03 3.65E+02 NO DATA 3.56E+03 2.21E+05 1.73E+05 W-187 8.48E+00 7.08E+00 2.48E+00 NO DATA NO DATA 2.90E+04 1.55E+05 HP-239 -2.30E+02 2.26E+01 1.24E+01 NO DATA 7.00E+01 3.76E+04 1.19E+05
- 1.26 x 10 3
- Less than 8.CO x 10-15 CLINTON-1 3-88 Rev.5-2/89 F
,, ,, . - , ._-.,,.+---.,-.--v - -
- , , , , , . , . , , , . ,_,7 . . - .
_ ~ . _ _ _ . . . . _ . _ . . _ _ _ _ _ _ _ _ - . - _ . _ . _ . _ _ . . _ . _ _ _ . _ _ _ _ _ . . _ _ . _
CPS-ODCM TABLE 3.5-17 C
COW MILK PATHWAY FACTORS Raij (INFANT)
(m2 mrem /yr per #Ci/sec) ,
ORCAN: M LIVER T. BODY Tir(ROID KIDNEY M CI-LLI 350 TOPE H3 NO DATA 2.38E+03* 2,38E+03* 2.38E+03* 2.38E+03* 2.38E+03* 2. 38E+03*
- 6. 89E+05* 6. 89E+05*
C 14 3.23E+06* '6.89E+05* 6'. 89 E+05* 6.89E+05* 6.89E+05*
NA 24 1,55E+07** 1.55E+07 1.55E+07 1.55E+07 1.55E+07 1.55E+07 1.55E+07 P 32 1.60E+11 3.41E+09 6.20E+09 NO DATA NO DATA NO DATA 2.16E+09 CR 51 NO DATA NO DATA 1.61E+05 1.0$E+05 2.29E+04 2.04E+05 4.69E+06 HN 54 NO DATA 3.90E+07 8.84E+06 NO DATA 8.64E+06 NO DATA 1.43E+07 MN-56 NO DATA 3.12E 02 5.39E 03 NO DATA 2.69E 02 NO DATA 2.84E+00 FE 55 1.35E+08 8.72E+07 2.33E+07 NO DATA NO DATA 4.26E+07 1.11E+07 FE 59 2.25E+08 3.92+08 1.55E+08 NO DATA NO DATA 1.16E+08 1.87E+08 Co 58 NO DATA 2.43E+07 6.06E+07 NO DATA NO DATA NO DATA 6.05E+07 CO 60 NO DATA 8.82E+07 2.08E+08 NO DATA NO DATA NO DATA 2.10E+08 NI-63 3.50E+10- 2.16E+09 1.21E+09 NO DATA NO DATA NO DATA 1.08E+08 i
NI-65 3.52E+00 3.98E 01 1.81E 01 NO DATA NO DATA NO DATA 3.03E+01 CU 64 NO DATA 1.84E+05 8.52E+04 NO DATA 3.11E+05 NO DATA 3.78E+06 EN+65 5.55E+09 1.91E+10 8.78E+09 NO DATA 9.23E+09 NO DATA 1.61E+10 ZN 69 1.94E-11 3.49E-11 2.60E 12 NO DATA 1.45E 11 NO DATA 2.S$E 09 BR 83 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA BR 84 NO DATA' NO DATA NO-DATA -NO DATA NO DATA NO DATA NO DATA BR 85 NO DATA NO DATA NO DATA 30 DATA NO DATA No DATA NO DATA RB 86 NO DATA- 2.23E+10 1.10E+10 NO DATA NO DATA NO DATA 5.70E+08 RB 88 NO DATA 1.88E-44. 1.03E 44 NO DATA NO DATA NO DATA 1.83E 44 RB-89 NO DATA 3.43E-52 2.36E 52 NO DATA NO DATA NO DATA 1.17E 52 SR-89 1.26E+10 NO DATA 3.61E+08 NO DATA NO DATA NO DATA 2,59E+08 SR 90 1.22E+11 -NO DATA 3.10E+10 NO DATA NO DATA NO DATA 1.52E+09 l
1 3R 91- 2.71E+05 NO DATA 9.76E+03 NO DATA NO DATA NO DATA 3.20E+05 SR-92 4.68E+00 NO DATA 1.74E 01 NO DATA NO DATA NO DATA 5.05E+01 Y 90 6.83E+02 NO DATA 1.83E+01 NO DATA NO DATA NO DATA 9.43E+05 CLINTON-1 3-89 Rev.5-2/89 y, , -vr-.... . , . , .- r ,, , . . , . - - - - , ,
CPS-ODCM '
7ABLE 'LJ-17 (continued)
COW MILK PATHWAY FACTORS - Raij (INFANT)
(m2 mrem /yr per pCi/sec)
ORCAth LME LIVER T. BODY THYROID KlMM MRUi CI-LLI ISOTOPE Y 91m 6.09E 19 NO DATA 2.08E 20 NO DATA NO DATA NO DATA 2.03E 15 Y-91 7.33E+04 NO DATA 1.95E+03 NO DATA NO DATA NO DATA 5.26E+06 Y 92 5.35E 04 NO DATA 1.50E 05 NO DATA NO DATA NO DATA 1.02E+01 Y 93 2.14E+00 NO DATA 5.83E 02 NO DATA NO DATA NO DATA 1.69E+04 ZR 95 6.82E+03 1.66E+03 1.18E+03 NO DATA 1.79E+03 NO DATA 8.28E+05 ZR 97 . 4.03EMO 6.96E 01 3.16E 01 NO DATA 7.01E 01 NO DATA 4.41E+04 NB-95 5.93E+05 2.44E+05 1.41E+05 NO DATA 1.75E+05 No DATA 2.06E+08 MO 99 NO DATA 2.07E+08 4.04E+07 NO DATA 3.10E+08 NO DATA 6.83E+07 T0 99m 2.75E+01 5.66E+01 7.29E+02 NO DATA 6.09E+02 2.96E+01 1.64E+04 TC 101 2.72E 59 3.42E 59 3.39E 58 NO DATA 4.07E-58 1.87E 59 5.81E 57 RU-103 - 8.67E+03 NO DATA 2.92E+03 NO DATA 1.81E+04 NO DATA 1.06E+05 RU-105 8.00E 03 NO DATA 2.70E-03 NO DATA 5.88E-02 NO DATA 3.18E+00 RU-106 1.91E+05 NO DATA 2.38E+04 NO DATA 2.26E+05 NO DATA 1.45E+06 AG 110m 3.85E+08 2.81E+08 1.86E+08 NO DATA 4.02E+08 NO DATA 1.46E+10 TE 125m 1.51E+08 5.05E+07 2.04E+07 5.08E+07 NO DATA NO DATA 7.19E+07 TE 127m 4.22E+08 1.40E+08 5.10E+07 1.22E+08 1.04E+09 NO DATA 1.70E+08 TE 127 6.31E+03 2.11E+03 1.39E+03 5.13E+03 1.58E+04 NO DATA 1.36E+05 TE-129m' 5.56E+08 1.91E+08 8.56E+07 2.14E+08 1.39E+09 NO DATA 3.32E+08 TE 129 2.71E 09 9.34E 10 6.33E-10 2.27E 09 6.75E 09 NO DATA 2.17E 07 TE-131m- 3.37E+06 1.36E+06 1.12E+06- 2.75E+06 9.35E+06 NO DATA 2.29E+07 TE 131 3.48E 32 1.29E 32 9.78E 33 3.11E 32 8.91E 32 'NO DATA 1.41E 30 TE 132 2.12E+07 1.05E+07 9.80E+06 1.55E+07 6.57E+07 NO DATA 3.89E+07 I 130 3.53E+06 7.76E+06 3.12E+06 6.70E+08 8.53E+06 NO DATA 1.66E+06 I 131 2.71E+09 3.19E+09 1.40E+09 1.05E+12 3.73E+09 NO DATA 1.14E+08 I 132 1.43E+00 2.90E+00 1.03E+00 1.36E+02 3.24E+00 NO DATA 2.35E+00 I 133 3.63E+07 5.28E+07 1.55E+07 9.60E+09 6.21E+07 NO DATA 8.93E+06 I 134 1.64E 11 3.36E-11 1.20E 11 7.86E-10 3.76E 11 NO DATA 3.48E 11 CLINTON-1 3-90 Rev.5-2/89
.n,s , ~ g , - , - -,, ,- y ,. g-., ,- ,,.,.,w-, ,--p_c~w- p.,-~ m - r.. un_,---wy m+
CPS-ODCM TABLE 3.5-17 (continued)
I COW HILK PATHWAY FACTORS - Raij (INFANT)
(m2 mrem /yr per gCi/sec)
ORGAN: LIVER T. BODY THYROID KIDNEY LlRig fd:lkl
]LQI!{E ISOTOPE 8.18E+04 2.01E+07 2.50EM5 NO DATA 8.12E+04 I 135 1.13E+05 2.24E+05 CS-134
- 65E+10
. 6.81E+10 6.88E+09 NO DATA 1.75E+10 7.19E+09 1.85E+08 CS 136 1.97E+09 5.81E+09 2.17E+09 NO DATA 2.31E+09 4.73E+08 8.82E+07 6.03E+10 4.27E+09 NO DATA 1.62E+10 6.55+09 1.89E+08 CS-137 5.15E+10 CS 138 8,06E 23 1.31E-22 6.35E 23 NO DATA 6.53E 23 1.02E 22 2.09E 22 BA 139 4.29E 07 2.84E-10 1.24E-08 NO DATA 1.71E 10 1.72E 10 2.72E 05 BA-140 2.45E+08 2.45E+05 1.26E+07 NO DATA 5.72E+04 1.50E+05 5.92E+07 BA-141 4.16E 45 2.85E-48 1.31E-46 NO DATA 1.71E 48 1.73E 48 5.08E 44 BA-142 2.32E-79 1.93E 82 1.14E 80 NO DATA 1.11E-82 1.17E.82 9.56E 79 1.60E+01 4.11E+00 NO DATA NO DATA NO DATA 1.88E+05 1A 140 4.05E+01 1.73E 10 6.34E 11 1.52E 11 NO DATA NO DATA NO DATA 1.08E 05 LA-142 2.65E+04 3.12E+03 NO DATA 8.17E+03 NO DATA 1.37E+07 CE 141 4.34E+04 2.64E+05 3.01E+01 NO DATA 7.69E+01 NO DATA 1.54E+06 CE-143 3.98E+02 9.56E+05 1.31E+05 NO DATA 3.87E+05 NO DATA 1.34E+08 CE 144 2.34E+06 5.56E+02 7.37E+01 NO DATA 2.07E+02 NO DATA 7.85E+05 PR-143 1.49E+03 6.27E-53 2.43E 53 3.16E 54 NO DATA 8.79E 54 NO DATA 1.13E 48 PR-144 9.03E+02 5.53E+01 NO DATA 3.48E+02 NO DATA 5.72E+05 ND 147 8.79E+02 6.10E+04 4.24E+04 1.46E+04 NO DATA NO DATA NO DATA 2.49E+06 W-187 3.26E+00 1.84E+00 NO DATA 6.49E+00 NO DATA 9.41E+04 NP 239 3.64E+01
- mrem /yr per gCi/m 3
- 1.55 x 10 7 CLINTON-1 3-91 Rev.5-2/89
,,- g r w-n---m -,.m r ,r,-,-, - , - - - , , , -. - , e .- - ,,w,y, - , , e-,- ~-m ,- + g , e
CPS-ODCM TABLE 3.5-18 COW MILK PATHWAY FACTORS - Raij (CHILD)
(m2 mrem /yr por pci/ soc)
ORGANt M LIVER T. BODY THYROID KIDNEY g CI LLI ISOTOPE H3 NO DATA 1.57E+03* 1.57E+03* 1.57E+03* 1.57E+03* 1.57E+03* 1. 57E+03*
C 14 1.65E+06* 3.29E+0$* 3.29E+05* 3.29E+0$* 3.29E+05* 3.29E+05* 3. 29E+0$*
NA 24 8.93E+06** 8.93E+06 8.93E+06 8.93E+06 8.93E+06 8.93c+06 8.39E+06 P-32 7.79E+10 3.64E+09 3.00E+09 NO DATA NO DATA NO DATA 2.15E+09 CR 51 NO DATA NO DATA 1.01E+05 5.63E+04 1.54E+04 1.03E+05 5.38E+06 MN 54 NO DATA 2.10E+07 5.59E+06 NO DATA 5.88E+06 NO DATA 1.76E+07 MN-56 NO DATA 1.28E 02 2.88E 03 NO DATA 1.54E 02 NO DATA 1.85E+00 FE 55 1.12E+08 5.94E+07 1.84E+07 NO DATA NO DATA 3.36E+07 1.10E+07 FE 59 1.20E+08 1.95E+08 9.71E+07 NO DATA NO DATA 5.65E+07 2.03E+08 Co 58 NO DATA 1.21E+07 3.71E+07 NO DATA NO DATA NO DATA 7.08E+07 CO 60 NO DATA 4.32E+07 1.27E+08 NO DATA NO DATA NO DATA 2.39E+08 NI 63 2.97E+10 1.59E+09 1.01E+09 NO DATA NO DATA NO DATA 1.07E+08
)HI65 1.65E+00 1.56E 01 9.10E 02 NO DATA NO DATA NO DATA 1.91E+01 CU 64 NO DATA 7.40E+04 4.47E+04 NO DATA 1.79E+05 NO DATA 3.47E+06 ,
ZN 65 4.13E+09 1.10E+10 6.83E+09 NO DA1A 6.92E+09 NO DATA 1.93E+09 ZN-69 9.11E 1.32E 11 1.22E 12 NO DATA 7.99E 12 NO DATA S.30E 10 BR 83 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA l BR 84 NO DATA NO DATA- NO DATA NO DATA NO DATA No DATA NO DATA !
BR 85 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA RB 86 NO DATA 8.78E+09 5.40E+09 NO DATA NO DATA NO DATA 5.65E+08 RB 88 NO DATA 7.16E 45 4.98E 45 NO DATA NO DATA NO DATA 3.51E 46 RB 89 NO DATA 1.40E 52 1.25E 52 NO DATA NO DATA NO DATA 1.22E 54 SR 89 6.63E+09 NO DATA 1.89E+08 NO DATA NO DATA NO DATA 2.57E+08 SR 90 1.12E+11 NO DATA 2.84E+10 NO DATA NO DATA NO DATA 1.51E+09 CLINTON-1 3-92 Rev.5-2/89
CPS-ODCM TABLE 3.5-18 (continued)
COW MILK PATHWAY FACTORS - Raij (CHILD)
(m2 mrem /yr per pCi/sec)
GI LLI !
ORGAN: SQEg LIVER T. BODY THYROID KIDNEY LIEQ iggTp1PE SR 91 1.30E+05 NO DATA 4.89EM3 NO DATA NO DATA NO DATA 2.86E+05 SR 92 2.20E+00 NO DATA 8.83E 02 NO DATA- NO DATA NO DATA 4.17E+01 Y 90 3.23E+02 NO DATA 8.65E+00 NO DATA NO DATA NO DATA 9.20E+05 Y 91m 2.88E 19 NO DATA 1.05E-20 NO DATA NO DATA NO DATA 5.63E 16 Y.91 3.90E+04 NO DATA l'04E+03
. NO DATA NO DATA NO DATA 5.20E+06 Y 92 2.53E 04 NO DATA 7.23E 06 NO DATA NO DATA NO DATA 7.30E+00 Y-93 1.01E+00 NO DATA 2.76E 02 NO DATA NO DATA NO DATA 1.50E+04 ZR 95 3.84E+03 8.44E+02 7.51E+02 NO DATA 1.21E+03 NO DATA 8.80E+05
' ZR 97 - 1.92E+00 2.78E 01 1.64E 01 NO DATA 3.99E 01 NO DATA 4.21E+04 NB 95 3.18E+05 1.24E+05 8.84E+04 NO DATA 1.16E+05 NO DATA 2.29E+08
- MO 99 NO DATA 8.15E+07 2.02E+07 NO DATA 1.74E+08 NO DATA 6.74E+07 TC 99m 1.32E+01 2.58E+01 4.28E+02 NO DATA 3.75E+02 1.31E+01 1.47E+04 1
TC-101 1.28E 59 1.34E 59 -1.70E 58 NO DATA 2.29E 58 7.08E 60 4.26E 59 RU 103 4.29E+03 NO DATA 1.65E+03 NO DATA 1.08E+04 NO DATA 1.11E+05 RU 105 3:80E 03 NO DATA 1.38E 03 NO DATA 3.34E 02 NO DATA 2.48E+00 RU 106 9.25E+04 NO DATA 1.15E+04 NO DATA 1.25E+05 NO DATA 1.44E+06 AG 110m 2.09E+08 1.41E+08 1.13E+08 NO DATA 2.63E+08 -NO DATA 1.68E+10 TE 125m 7.39E+07. 2.00E+07 9,85E+06 2.07E+07 NO DATA NO DATA 7.13E+07-TE 127m 2.08E+08 5.61E+07 2.47E+07 4.9CE+07 5.94E+08 NO DATA 1.69E+08 TE-127 - 2.97E+03 8.01E+02 6.37E+02 2.06E+03 8.45E+03 NO DATA 1.16E+05 TE 129m 2.71E+08- 7.58E+07 4.21E+07 8.74E+07 7.97E+08 NO DATA 3.31E+08 TE 129 1.28E 09 3.57E 10- 3-04E 10
. 9.12E 10 3.748 09 No DATA 7.96E-08
- TE 131m 1.60E+06 5.53E+05 5.88E+05 1.14E+06 5.35E+06 NO DATA 2.24E+A7
~TE 131 1,64E 32 5.01E-33 4.89E 33 1.26E 32 4.97E-32 NO DATA 8.63E 32 n.
TE 132 1.03E+07 4.56E+06 5.51E+06 6.64E+06 4.23E+07 NO DATA 4.59E+07 3.82E+08 5.19E+06 NO DATA 1,62E+06 I-130 . 1.72E+06 3.47E+06 1.79E+06 I 131 1.30E+09 1.31E+09 7 . M E+08 4.33E+11 2.15E+09 NO DATA 1.17E+08 l
l CLINTON-1 3-93 Rev 5-2/89 w-, ~,-,# ,,y ,w.- ,.gw.- .,mv m,,,-- [ - #, _ww.em-.c,_ .,_.,_.nmw_. , , _ _ , .
CPe 0DCM TABLE 3.5-18 (continued)
COW MILK PATl!WAY FACTORS - Raij (Cl!ILD)
(m2 mrem /yr per pCi/sec)
ORCAN: M LIVER T. BODY THYROID KIDNEY M CI LLI ISOTOPE I 132 6.91E 01 1.27E+00 5.84E 01 5.89E+01 1.94E+00 NO DATA 1.49E+00 I 133 1.72E+07 2.12E+07 8.03E+06 3.94E+09 3.54E407 NO DATA 8.56E+06 I 134 7.92E 12 1.47E 11 6.77E 12 3.38E-10 2.25E 11 NO DATA 9.75E 12 1 135 5.43E+04 9.77E+04 4.62E+04 8.56E+06 1.50E+05 NO DATA 7.44E+04 CS 134 2.27E+10 3.72E+10 7.85E+09 NO DATA 1.15E+10 4.14E+09 2.01E+08 CS 136 1.01E+09 2.78E+09 1.80E+09 NO DATA 1.48E+09 2.21E+08 9.76E+07 CS 137 3.23E+10 3.09E+10 4.56E+09 NO DATA 1.01E+10 3.63E+09 1.94E+08 CS 138 3.82E 23 5.31E 23 3.37E 23 NO DATA 3.74E-23 4.02E 24 2.45E 23 BA 139 2.01E 07 1.08E 10 5.84E 09 NO DATA 9.39E 11 6.33E 11 1.16E 05 BA 140- 1.18E+08 1~.03E+05 6.84E+06 NO DATA 3.37E+04 6.12E+04 5.94E+07 BA 141 1.96E 45 1.10E 48 6.38E-47 NO DATA 9.50E-49 6.45E 48 1.12E-45 BA 142 1.10E 79 7.93E 83 6.15E-81 NO DATA 6.41E.83 4.66E 83- 1.44E-01 f LA 140 6.78E+00 2.11E+00 NO DATA NO DATA 1.893+95 1.94E+01 NO DATA IA 142 8.23E 11 2.62E 11 8.21E-12 NO DATA NO DATA NO DATA 5.20E 06 CE 141 2.19E+04 1.09E+04 1.62E+03 NO DATA 4.78E+03 NO DATA 1.36E407
-CE-143 1.87E+02 1.02E+05 1.47E+01 NO DATA 4.26E+01- NO DATA 1.49E+06 CE 144 1.63E+06 5.10E+05 8.68E+04 NO DATA 2.82E+05 NO DATA 1.33E+08 PR 143 7.19E+02 2.16E+02 3.57E+01 NO DATA 1.17E+02 NO DATA 7.76E+05 PL 144 2.94E 9.10E 54 1.48E-54 NO DATA. 4.81E 54 NO DATA 1,96E-50 ND 147 4.44E+02 3.59E+02 2.78E+01 NO DATA 1.97E+02 60 DATA 5.69E+05 V-187 2.88E+04 1.71E+04 7.66E+03 NO DATA ~ ' NO DATA NO DI.TA 2.40E+06 NP 239 1.72E+01 1.24E+00 8.69E 01 NO DATA 3.58E+00 PO DATA 9.15E+04
- mrem /yr por #C1/m 3
- 8.93 x 10 6 CLINTON-1 3 94 Rev.6'.12/89
,i. y - . ,-uwm.- -m,.:.. ,.es . r...c,----,-.r- r -er-w- , - - r eme n.v,,,v--- rwme-,-r-mn.=-
CPS-0DCM TABLE 3.5-19 COW MILK PATHWAY FACTORS - Raij (TEEll)
(n2 mrem /yr per pCi/sec)
ORGAN! EQlig M T BODY THYROID KIDNEY lE!Q GI-LLI ISOTOPE H3 NO DATA . 9.92E+02* 9.92E+02* 9.92E+02* 9.92E+02* 9.92E+02* 9.92E+02*
C 14 6.70E+05* 1.34E+05* 1.34E+05* 1.34E+05* 1.34E+0$* 1.34E+05* 1.34E+0$*
NA 24 4.29E+06* 4.29E+06 4.29E+06 4.29E+06 4.29E+06 4.29E+06 4.29E+06 P 32 3.15E+10 1.95E+09 1.22E+C9 NO DATA NO DATA NO DATA 2.64E+09 CR 51 NO DATA NO DATA 5.00E+04 2.78E+04 1.10E+04 7.14E+04 8.41E506 MN NO DATA 1~.40E+07 2.78E+06 NO DATA 4.19E+06 NO DATA 2.88E+07 MN-56 NO DATA 7.32E 03 1.30E-03 NO DATA 9.26E 03 NO DATA 4.82E 01 i FE-55 4.46E+07 3.16E+07 7.38E+06 NO DATA NO DATA 2.01E+07 1.37E+07 FE 59 5.18E+07 1.21E+08 4.67E+07 NO DATA No DATA 3.81E+07 2.86E+08 CO 58 NO DATA 7,98E+06 1.84E+07 NO DATA NO DATA NO DATA 1.10E+08 CO 60 NO DATA 2.78E+07 6.26E+07 NO DATA NO DATA NO DATA 3.62E+08 NI 63 1.18E+10 8.34E+08 4.00E+08 NO DATA NO DATA NO DATA 1.33E+08
)
Ni 65 6.79E 01 8.67E 02 3.95E 02 NO DATA NO DATA NO DATA 4.70E+00 Cu 64 NO DATA 4.20E+04 1.97E+04 NO DATA 1.06E+05 NO DATA 3.26E+06 Zn 65 2.11E+09 7.32E+09 3.41E+09 NO DATA 4.68E+09 NO DATA 3.10E+09
~ ZN 69 3.70E 12 7.06E 12 4.94E 13- NO DATA 4.61E 12 NO DATA 1.30E 11 BR 83 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA BR 84 -NO DATA- NO DATA NO DATA NO DATA -NO DATA NO DATA NO DATA BR-85 NO DATA NO DATA NO DATA NO DATA HO DATA NO DATA NO DATA RB 86 NO DATA 4.74E+09 2.23E+09 NO DATA NO DATA NO DATA 7.01E+08 RB-88 NO DATA 3.9CE 45 2.0dE 45 NO DATA NO DATA NO DATA 3.34E-52 RB 89 NO DATA 7.98E 53 5.64E 53 NO DATA NO DATA NO DATA 1.225-61.
SR 89 2.68E+09 NO DATA 7.67E+07 NO DATA NO DATA NO DATA 3.19E+08 SR-90 6.6kE+10 NO DATA 1.64E+10 NO DATA NO DATA NO DATA 1.86E+09-SR-91 5.27E+04 NO DATA 2.10E+03 NG DATA NO DATA NO DATA 2.39E+05 SR-92 9,03E 01 NO DATA 3.85E 02 NO DATA NO DATA NO DATA 2.30E+01 Y-90 -1,31E+02 NO DATA 3.53E+00 NO DATA NO DATA NO DATA 1.0BE+06 CLINTON-1 3-95 Rev.5-2/89
_- _ _ _ = _ = - _ _ _ - _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ - _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ .
CPS 0DCM TABLE 3.5-19 (continued)
COW MILK PATINAY FACTORS - R aij (T m 0 (m2 mrem /yr por pCi/ soc)
ORGAN:. E LIVER T. BODY TINROID KIDNEY M GI-LLI ISOTOPE Y 91m 1.18E.19 "O DATA 4.49E 21 NO DATA NO DATA NO DATA 5.55E 18 Y 91 1.58E+04 No DATA 4.24E+02 NO DATA NO DATA No DATA 6.48E+06 Y.92 1.03E 04 NO DATA 2.97E 06 NO DATA NO DATA NO DATA 2.82+00 Y 93 4.10E 01 NO DATA 1.12E 02 NO DATA NO DATA NO DATA 1.25E+04 ZR.95 1.65E+03 5.20E+02 3.58E+02 NO DATA 7.65E+02 NO DATA 1.20E+06 ZR 97 '7.87E 01 1.56E.01 7.17E 02 NO DATA 2.36E 01 NO DATA 4.22E+04 '
NS 95 1.41E+05 7.81E+04 4.30E+04 NO DATA 7.57E+04 NO DATA 3.34E+08 MO 99 NO DATA 4.46E+07 8.50E+06 NO DATA 1.02E+08 NO DATA 7.98E+07 TC 99m 5.74E+00 1.60E+01 2.08E+02 NO DATA 2.39E+02 8.89E+00 1.05E+04 TC.101 5.22E.60 7.42E 60 7.29E-59 NO DATA 1.34E-58 4.52E.60 1.27E.66
-RU-103 1.81E+03 NO DATA 7.73E+02 -NO DATA 6.37E+03 NO DATA 1.51E+05 RU 105 1.56E 03 NO DATA 6.06E 04 NO DATA 1.97E 02 NO DATA 1.26E+00 RU.106 3.75E+04 NO DATA 4,73E+03 NO DATA 7.23E+U4 NO DATA 1.80E+06 AG.110m 9.64E+07 9.12E+07 5.55E+07 NO DATA 1.74E+08 NO DATA 2.56E+10 TE 125m 3.01E+07 1.08E+07 4.02E+06 8.41E+06 NO DATA NO DATA 8.88E+07
-TE.127m' 8.43Et07 2.99E+07 1.00E+07 2.01E+07 3.42E+08 NO DATA 2.10E+08 TE.127 1.21E+03 4. 2 8 5'+02 2.60E+02 8.33E+02 4.89E+03 NO DATA 9.33E+04 TE 129m 1.10E+08 '4.' -1.74E+07 3.56E+07 4.61E+08 NO DATA 4.14E+08 ;
TE.129 5.18E 10 1.93E 10 1.26E 10 3.70E 10 2.17E 09 NO DATA 2.83E 09 TE.131m 6.56E+05 - 3.15E+05 2.63E+05 - 4.73E+05 3.28E+06 NO DATA 2.53E+07 TE.131 6.70E-33 2.76E 33 2.09E 33 5.16E 33 2.93E-32 NO DATA 5.50E 34 TE 132 4.29E+06 2.72E+06 2.56E+06 2.87E+06 2.61E+07 NO DATA 8.61E+07 1 130 7.33E+05 2.12E+06 8,47E+05 1.73E+00 3,27E+06 NO DATA 1.63E+06 I.131 5.36E+08 7.50E+08 4.03E+08 2.196+11 1.29E+09 NO DATA 1 ASE+08 I 132 2.90E 01 7.59E 01 2.72E 01 2.56E+01 1,20E+00 NO DATA 3.31E 01 1 133 7'06E+06 1.20E+07 3.65E+06 1.67E+09 2.10E+07 NO DATA 9.06E+06 I 134 3.34E 12 8.86E 12 ' 3.18E-12 1.48E 10 1.40E-11 NO DATA 1.17E 13 C1.INTON-1 3 96 Rev.5-2/89
-wn, .47 y 'rr-v--ww-y,y, c y- . , ~ .m'ew,--,w,-em.w'v,',-w,. ,,[, .yy. . - - - E -E % 4w. a,---,se,-,c----.,-,,,wmy.-,1.m.,.,,cw_,w,.w,.,.-m_.,,y.-,c,.r-,.-...,2,,%,-
TCPS 0DCF.
TABLE 3.5-19 (continued 1 COW MILK PATHWAY FACTORS - Raij (TEEN)
(m2 mrem /yr per pCi/sec)
LIVER T. BODY THYROID KIDNEY 121G, CI-LLI ORCAN: lQHE i ISOTOPE 5.90E+04 2.19E+04 3.80E+06 9.32E+04 NO DATA 6.54E+04 I-135 2,29E+04 2.87E+08 CS 134 9.79E+09 2.30E+10 1.07E+10 NO DATA 7.32E+09 2.80E+09 4.48E+08 1.76E+09 1.18E+09 NO DATA 9.59E+08 1.51E+08 1.42E+08 CS 136 1.33E+1b 7E+10 6.18E+09 NO DAfA 6.03E+09 2.34E+09 2.52E+08 CS 131 CS-138 1.58E 23 3.03E-23 1.51E 23 NO DATA 2.23E-23 2.60E 24 1.37E-26 8.20E 08 5.7.'E 11 2.39E-09 NO DATA 5.44E 11 3.98E 11 7.31E 07 BA-139 l 4.85E+07 5.95E+04 3.13E+06 NO DATA 2.02E404 4.00E+04 7.49E+07 BA-140 7.98E 46 5.76E-49 2.67E 47 NO DATA 5.53E-49 4.08E-49 1.70E-51 BA-141 4.54E-80 4.54E-83 2.8CE 81 NO DATA 3.85E-83 3.02E-83 1.40E-91 BA-142 8.11E+00 3.98E+00 1.06E+00 NO DATA NO DATA NO DATA J 99E+05 LA-140 o,62E 07 3.42E-11 1.52E-11 3.78E-12 NO DATA NO DATA NO DATA LA-142 1.70E+07 CE-141 8.88E+03 5.93E+03 6.81E+02 NO DATA 2.79E+03 NO DATA i
5 55E+04 6.21E+00 NO DATA 2.49E+01 NO DATA 1.67E+06 CE 143 7.64E+01 2.7:5+05- 3.55E+04 NO DATA 1.63E+05 NO DATA 1.66E+08 CE 144' 6.61E+05 1.16E+02 1.45E+01 NO DATA 6.75E+01 NO DATA 9.57E+05 PR 143 2.91E+02 1.19E 53 4.88E-54 6.04E-55 NO DATA. 2.80E-54 NO DATA 1.31E-56 PR-144 1.97E+02 1.18E+01 NO DATA 1.16E+02 NO DATA 7.10E+05 ND-147 1.81E+02 9.72E+03 3.41E+03 NO DATA NO DATA NO DATA 2.63E+06 W-187 1.19E+04 6.59E-01 3.66E-01 NO DATA 2.07E+00 "C DATA 1.06E+05 Nr-239- 6.99E+00 4
- mrem /yr per pCi/m 3
- 4 29 x l'06 CLINTON-1 3-97 Rev.5-2/89
u s .2 vu.
TABLE 3.5-20 COW MILK PATHWAY FACTORS - R C (ADULT)
(m2 mren/yr per pCi/sec)
ORGAN: EG{g LlyJE L.3@X THYROID KIDNEY Ii'JiQ Cl LLI ISOTOPE H3 NO DATA 7.62E+02* 7.62E+02* 7.62E+02* 7,62E+02* 7.62E+02* 7.62E+02*
J 14 3.63E+05* 7.26E+04* 7.26E+04* 7.26E+04* 7.26E+04* 7.26E+04* 7.26E+04*
NA 24 2.46E+06** 2.46E+06 2.46E+06 2.46E+06 2.46E+06 2.46E+06 2.46E+06 P-32 1.71E+10 1.06E+09 6.61E+0B NO DATA NO DATA NO DATA 1.92E+09 CR 51 NO DATA NO DATA 2.85E+04 1.70E+04 6.27E+03 3.78E+04 7.16E+06 HN-54 NO DATA 8.41E+06 1.60E+06 NO DATA 2.50E+06 NO DATA 2.58E+07 MN-56 NO DATA 4.14E 03 7.34E-04 NO DATA 5.26E-03 NO DATA 1.32E 01 FE-55 2.51E+07 1.73E+07 4.04E+06 NO DATA NO DATA 9.68E+06 9.95E+06 FE 59 2.97E+07 6.99E+07 2.68E+07 NO DATA NO DATA 1.95E+07 2.33E+08 CO-58 NO DATA 4.72E+06 1.06E+07 NO DATA NO DATA NO DATA 9.57E+07 CO-60 NO DATA 1.64E+07 3.62E+07 NO DATA NO DATA NO DATA 3.08E+08 6.73E+09 4.67E+08 2.26E+08 NO DATA NO DATA NO DATA 9.74E+07
)NI-63 NI-65 3.70E-01 4.81E 02 2.19E-00 NO DATA NO DATA NO DATA 1.22E+00 CU-64 NO DATA 2.36E+04 1.llE+04 NO DATA 5.94E+04 NO DATA 2.01E+06 ZN-65 1.37E+09 4,37E+09 1.98E+09 NO DATA 2.93E+09 NO DATA 2.75E+09 ZN 69 2.01E-12 3.84E-12 2.67E-13 NO DATA 2.50E 12 NO DATA 5.77E-13 -
BR-83 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA BR-84 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA BR-85 NO DATA NO DATA NO DAh NO DATA NO DATA NO DATA NO DATA RS-86 NO DATA 2.60E+09 1.21E+09 NO DATA NO DATA NO DATA 5.12E+08 RB-88 NO DATA 2.15E-45 1.14E-45 NO DATA NO DATA NO DATA 2.97E-56 R2-89 NO DATA 4.49E-53 3.16E-53 NO DATA NO DATA NO DATA 2.61E 66 SR-89 1.45E+09 NO DATA 4.16E+07 NO DATA NO DATA No DATA 2.33E+08 SR-90 4.68E+10 NO DATA 1.15E+10 NO DATA NO DATA NO DATA 1.35E+09 SR-91 2.87E+04 NO DATA 1.16E+03 NO DATA NO DATA NO DATA 1.37E+05 SR-92 4.92E-01 NO DATA 2.13E-02 NO DATA NO DATA NO DATA 9.76E+00 Y-90 7.10E+01 NO DATA 1.90E+00 NO DATA NO DATA NO DATA 7.53E+05 CLINTON-1 3-98 Rev.5-2/89 l
l
. CPS 30DCM
{
1
-TABLE 3.5-20 (continued)
C COW MILK PATHWAY FACTORS - R (ADULT) i (m2 mrem /yr per pCi/sec)
ORGANt HQEE LIVER T. BODY THYROID KIDNEY IAR{G GM' LSQJ0PE-
- Y-91m- 6.42E 20 NO DATA 2.49E-21 UO DATA NO DATA NO DATA 1.89E-19 2.30E+02 NO DATA NO DATA NO DATA 4.73E+06 Y-91 8.60E+03
- NO DATA 5.57E 05 NO DATA 1.63E-06 NO DATA NO DATA NO DATA 9.75E 01 Y 92 2.22E-01 NO DATA 6.12E-03 NO DATA NO DATA NO DATA 7.03E+03
.Y 93 9.61E+05 9.45E+02 3.03E+02 2.05E+02 NO DATA 4.76E+02 NO DATA 8,71E-02 3.98E-02 NO DATA 1.32E-01 NO DATA 2.70E+04 4 ' a 4.32E-01 4.59E+04 2.47E+04 NO DATA 4.54E+04 NO DATA 2.79E+08 8.25E+04 4.72E+06 NO DATA 5.61E+07 NO DATA 5.74E+07 NO DATA 2.48E+07 5.53E+03
-3,31E+00 9.35E+00 1.19E+02 NO DATA 1.42E+02 4.58E+00 2.85E 4.11E-60 4.03E-59 NO DATA 7.41E-59 2.10E-60 1.24E-71 TC-101 1.19E+05 1.02E+03 NO DATA 4.39E+02 NO DATA 3.'89E+03 NO DATA RU-103 3.36E-04 NO DATA 1.10E-02 NO DATA 5.21E-01
.RU-105 8.52E-04 NO DATA
)
NO DATA 2.58E+03 NO DATA 3.94E+04 NO DATA 1.32E+06 RU 106 2.04E+04 5.39E+07 3.20E+07 NO DATA 1.06E+08 NO DATA 2.20E+10 A0 110m 5.82E+07 5.91E+06 2.19E+06 4.91E+06 6.64E+07 NO DATA 6.52E+07 TE-125m 1.63E+07 1,64E+07 5.58E+06 1.17E+07 1.86E+08 NO DATA 1.53E+0S TE 127m 4.58E+07 2.34E+02 1.41E+02 4.83E+02 2.65E+03 NO DATA 5.14E+04
-TE-127 6.52E+02 2.24E+07 9.52E+06 2,07E+07 2.51E+08 NO DATA 3.03E+08 TE-129m 6'.01E+07 1.06E-10 6.86E-11 2.16E-10 1.18E-09 NO DATA 2.12E-10 TE-129 2.82E-10 1.76E+05 1.47E+05 -2.79E+05 1.78E+06 NO DATA 1.75E+07 TE 131m 3.60E+05 1.54E-33 1.16E 3.03E 33 1.61E-32 NO DATA 5.22E 34 TE-131 3.68E-33 1,46E+06 1.72E+06 1.50E+07 NO DATA 7.36E+07-
.TE 132 2.41E+06 1.56E+06 l
1.23E+06- 4.84E+05 1.04E+08 1.91E+06 NO CATA 1.06E+06
_ 1-130 '4.16E+05 l:
4.24E+08 2.43E+08 1.39E+11 7.27E+08 NO DATA 1.12E+08
'I-131. 2.97E+08 4.40E-01 1.54E-01 1.54E+01 7.02E-01 NO DATA 8.27E-02
, I-132 1.65E-01 6.04E+06 6.72E+06 2.05E+06 9.87E+08 1.17E+07 NO DATA I-133 3.86E+06 NO DATA '.47E-15 I-134- 1.89E-12 5.13E-12 1.83E-12 8.88E-11 8.15E-12 +
CLINTON-1 3-99 Rev.5-2/89 l
wr o ww.
l TABLE 3.5-20 (continued)
C COW MILK PATHWAY FACTORS - R (ADULT)
(m2 mrem /yr per pCi/sec)
ORGAN- JLQllE LIVER T. BODY THYROIQ KIDNEY LtRiG GI-LLI ISOTOPE Z-135 1.296+04 3.39E+04 1.25E+04 2.23E+06 5.43E+04 NO DATA 3.83E+04 CS 134 5.67E+09 1.35E+10 1.10E+10 NO DATA 4.37E+09 1.45E+09 2.36E+08 CS-136 2.64E+08 1.04E+09 7.49E+08 NO DATA 5.79E+08 7.94E+07 1.18E+08 CS 137 7.39E+09 1.01E+10 6.62E+09 NO DATA 3.43E+09 1.14E+09 1.96E+08 CS-138 8.69E-24 1.72E-23 8.50E-24 NO DATA 1.26E 23 1.24E-24 7.32E 29 BA 139 4.43E-08 3.16E-11 1.30E-09 NO DATA 2.95E-11 1.79E-11 7.86E-08 DA-140 2.72E+07 3.42E+04 1.78E-06 NO DATA 1.16E+04 1.96E+04 5.60E+07 BA-141 4.33E 46 3.27E-49 1.46E-47 NO DATA 3.04E 49 1.86E 49 2.04E-35 BA-142 2.51E 80 2.58E-83 1.58E-81 NO DATA 2.18E 83 1.46E-83 3.54E-98 IA- 1.40 4.53E+00 2.28E+00 6.03E-01 NO DATA NO D/.TA NO DATA 1.67E+05 LA-142 1.89E-11 8.61E-12 2.15E 12 NO DATA NO DATA NO DATA 6.29E-08 CE 141 4.84E+03 3.27E+03 3.71E+02 NO DATA 1.52E:03 NO DATA 1.25E+07
)
CE-143 4.16E+01 3.07E+04 3.40E+00 NO DATA 1.35E+01 NO DATA 1.15E+06 CE-144 3.58E+05 1.50E+05 1.92E+04 NO DATA 8.87E+04 NO DATA 1.21E+08 PR-143 1.58E+02 6.35E+01 7.84E+00 NO DATA 3,66E+01 NO DATA 6.93E+05 PR-144 6.47E-54 2.69E-54 3.29E-55 NO DATA 1.52E-54 NO DATA 9.31E-61 ND-147 9.44E+01 1.09E+02 6.53E+00 NO DATA 6.38E+01 NO DATA 5.24E+05 W-187 6.50E+03 5.43E+03 1.90E+03 NO DATA NO DATA NO D/<TA 1.78E+06 4
NP-239 3.67E+00 3.60E-01 1.99E-01 NO D.iTA 1.12E+00 NO DATA 7.39E+04
- mrem /yr per pCi/n3
- 2.46 x 10 6 CLINTON-1 3 100 Rev.5-2/89
_- ~ .- . , . - - - . .. - . . - . - ~ .. .~ , _ . . - . - - -
CPS-0DCM TABLE 3.5-21 C
GOAT MILK PATHWAYLFACTORS - R (INFANT)
(m2 mrem /yr per pCi/sec)
LIVER T. BODY THYROID KIDNEY M[H.Q GI-LLI ORGAN: HDE ISOTOPE-
- H3 NO DATA. 4.86E+03* 4.86E+03* 4.86E+03* 4'.86E+03* 4.86E+03* 4.86E+03*
C 14 3.23E+06* 6.89E+05* . 6.89E+05* 6.89E+05* 6.89E+05* 6.89E+05* 6.89E+05*
NA-24 1.87E+06** 1.87E+06 1.87E+06 1.87E+06 1.87E+06 1.87E+06 1.87E+06
.P 32 1.90E+11 1.12E+10 7.46E+09 NO DATA NO DATA NO DATA 2.58E+09 CR-51 NO DATA NO DATA 1.93E+04 1.26E+04 2.75E+03 2.45E+04 5.63E+05 MN-54 NO DATA 4.68E+06 1.06E+06 NO DATA 1.04E+06 NO DATA 1.72E+06 MN-56 NO DATA 3.75E-03 6.46E-04 NO DATA 3.22E-03 NO DATA 3.40E 01 FE-55 1.75E+06 1.13EM 6 3.02E+05 NO DATA NO DATA 5.53E+05 1.44E+05 FE-59: 2.91E+06 5.08E+06 2,00E+06 NO DATA NO DATA 1.50E+06 2.43E+06 CO-58 NO DATA 2.90E+06 7.24E+06 NO DATA NO DATA NO DATA 7.23E+06 CO-60 .NO DATA- 1.06E+07 2.49E+07 NO DATA NO DATA NO DATA 2.51E+07 NI-63 4.19E+09 2.59E+08 1.45E+08 NO DATA NO DATA NO DATA 1.29E+07
)
NI 65 4.20E-01 4.76E-02 2.16E-02 NO DATA NO DATA NO DATA 3.62E+00 CU-64 NO DATA 2.04E+04 9.45E+03 NO DATA 3.45E+04 NO DATA 4.19E+05 ZN-65 6.64E+08 2.28E+09 1.05E+09 NO DATA 1.10E+09 NO DATA 1.92E+09 3.11E-13 1.74E-12 NO DATA 3,41E-10 ZN-69 2.32E-12 4.18E-12 NO DATA BR-83 NO DATA NO DATA NO DATA NO DATA NO DATA NO' DATA NO DATA
- BR-84 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA _
=BR-85 NO DATA NO DATA NO DATA NO DATA' NO-DATA NO DATA NO DATA
- RB-86 NO DATA 2.65E+09 1.31E+09 NO DATA NO DATA NO DATA 6.79E+07
'RB-88 :NO DATA .2.25E-45 1.23E 45 NO DATA NO DATA NO DATA 2.19E-45 lc l -RB 89- NO DATA 4.09E-53 -2.82E-53 NO DATA NO DATA NO DATA 1.39E-53
-SR-89 '2.64E+10 NO DATA 7.56E+08 NO DATA NO DATA NO DATA 5.42E+08 SR-90 ~2.55E+11 NO DATA 6 ~. 50 E+10 NO DATA NO DATA NO DATA 3.19E+09 >
! ' SR- 91' 5.65E+05 NO DATA 2.05E+04 NO DATA NO DATA NO DATA 6.69E+05 l SR 92 9.33E+00 NO DATA 3.65E-01 NO DATA NO-DATA NO DATA 1.06E+02 Y-90 8.19E+01 NO DATA 2.19E+00 NO DATA NO DATA NO DATA 1.13E+05 CLINTON 3-101 .Rev.5 2/89 l
TABLE 3.5-21 (continued)
C GOAT MILK PATIIWAY FACTORS -R (INFANT)
(m2 mrem /yr per pCi/sec)
T. BODY THYROID KIDNEY 11"dq GI-LLI ORGAN: DDE LIVER ISOTOPE 2.*BE 21 NO DATA NO DATA NO DATA 2.43E 16 Y 91m 7.29E-20 NO DATA NO DATA 6.29E+05 NO DATA 2.34E+02 NO DATA NO DATA
't - 91 8.78E+03 1.22E+00 1.80E 06 NO DATA NO DATA NO DATA Y 92 6.40E-05 NO DATA 6.95E 03 NO DATA NO DATA NO DATA 2.02E+03 Y-93 2.55E-01 NO DATA NO DATA 9.90E+04 2R-95 8.16E+02 1.99E+02 1.41E+02 NO DATA 2.14E+02 3.80E 02 NO DATA 8.40E 02 NO DATA 5.31E+03 ZR 97 4.85E-01 8.33E 02 1.69E+04 NO DATA 2.10E+04 NO DATA 2.47E+07 NB-95 7.12E+04 2.93E+04 4.84E+06 NO DATA 3.71E+07 NO DATA 8.18E+06 MO 99 NO DATA 2.48E+07 8.67E+01 NO DATA 7.24E+01 3.52E+00 1.96E+03 TC-99m 3.26E+00 6.73E+00 4.06E-59 NO DATA 4.88E-59 2.24E-60 6.98E-58 TC-101 3.26E-60 4.11E-60 1,26E+04 NO DATA 3.47E+02 NO DATA 2.16E+03 NO DATA RU-103 1.04E+03 3.82E-01 RU-105 9.60E-04 NO DATA 3.23E'-04 NO DATA 7.06E-03 NO DATA
) 1.73E+05 NO DATA 2.84E+03 NO DATA 2.69E+04 NO DATA RU-106 2.28E+04 1.75E+09 AG-110m 4.62E+07 3.37E+07 2.23E+07 NO DATA 4.83E+07 NO DATA 6.06E+06 NO DATA NO DATA 8.58E+06 TE-125m 1.80E+07 6.02E+06 2.43E+06
- 1. 46 E+07 1.24E+08 NO DATA 2.03E+07 TF U7m 5.04E+07 1.67E+07 6.10E+06 6.16E+02 1.85E+03 NO DATA 1.59E+04
^
17 7.57E+02 2.54E+02 1.63E+02 1.03E+07 2.57E+07 1,67E+08 NO DATA 3.99E+07 TE-129m 6.68E+07 2.29E+07 7.59E-11 2.73E-10 8.10E-10 NO DATA 2.60E-08 TE 129 3.25E-10 1.12E-10 2.74E+06 1.34E+05 3.30E+05 1.12E+06 NO DATA TE 131m 4.04E+05 1.63E+05 1.18E-33 3,74E-33 1.07E-32 NO DATA 1.69E-31 TE 131 4.19E-33 1.55E-33 1.17E+06 1.85E+06 7,86E+06 NO DATA 4.65E+06 TE-132 2.54E+06 1.26E+06 3.73E+06 1.04E+09 1.02E+07 NO DATA 1.99E+06 I-130 4.22E+06 9.2BE+06 1.37E+08 1.69E+09 1,26E+12 4.48E+09 NO DATA I-131 3.25E+09 3.83E+09 1.64E+02 3.91E+00 NO DATA 2.84E+00 I-132 1.73E+00 3.50E+00 1.25E+00 1.15E+10 7.43E+07 NO DATA 1.07E&O7 I-133 4.34E+07 6.32E+07 1.85E+07 4,04E-11 1.44E ll 9.42E-10 4.52E-11 NO DATA 4.18E-ll I-134 1.97E-11 3-102 Rev.5-2/89 CLINTON-1
cra vuun l
TABLE 3.5-21 (contir.ued)
GOAT MILK PATHWAY FACTORS - R C (INFANT) ,!
(m2 mrem /yr per pCi/sec)
ORGAN: LIVER T.BODi THYROID KIDNEY L]SiG CI-LLI SQFJ ISOTOPE 9.77E+04
=
I-135 1.36E+05 2.70E+05 9.85E+04 2.42E+07 .01E+05 NO DATA CS 134 1.09E+11 2.04E+11 2.06E+10 NO DATA . 25E+10 2.15E+10 5.54E+08 CS-136 5.92E+09 1.74E+10 6.50E+09 NO DAT/ 6.94E+09 1.42E+09 2.64E+08 CS-137 1.54E+11 1.80E+11 1.28E+10 NO DATA 4.84E+10 1.96E+10 5.63E+08 CS-138 2.42E-22 3.93E-22 1.90E-22 NO DATA 1.96E 22 3.06E 23 6.28E 22 BA-139 5.14E-08 3.41E 11 1.49E-09' NO DATA 2.05E-11 2.07E-11 3,26E 06 BA-140 2.87E+07 2.87E+04 1.48E+06 NO DATA 6.82E+03 1.76E+04 7.06E+06 BA-141 4.97E-46 3.40E-49 1.57E 47 NO DATA 2.05E-49 2.07E-49 6.07E-45 BA 142 2.76E-80 2.30E-83 1.36E 81 NO DATA 1.32E-83 1.39E-83 1.14E 79 i
L LA-140 4.83E+00 1.91E+00 4.90E-01 NO DATA NO DATA NO DATA 2.24E+04 1A-142 2.07E-11 7.60E-12 1.82E-12 NO DATA NO DATA NO DATA 1.29E-06 l
l CE 141 -5.20E+03 3.17E+03 3.73E+02 NO DATA 9.78E+02 NO DATA 1.64E+06
).
L CE-143 4.75E+01 3.15E+04 3.60E+00 NO DATA 9.18E+00 NO DATA 1.84E+05 CE-144 2.79E+05 1.14E+05 1.56E+04 NO DATA 4.61E+04 NO DATA 1.60E+07
'PR 143 1.78E+02 6.66E+01 8.83F+00 NO DATA 2.47E+01 NO DATA 9.40E+04 PR-144 7.51E-54 2.90E-54 3.78E 55 NO DATA 1.05E-54 NO DATA 1.35E 49
.ND-147 1.06E+02 1.08E+02 6.65E+00 NO DATA 4.18E+01 NO DATA 6.88E+04 W-187 7.27E+03 5.06E+03 1.75E+03 NO DATA NO DATA NO DATA 2.97E+05 l-l NP-239 4.37E+00- 3.91E-01 2.21E-01 NO DATA 7.80E-01 NO DATA 1.13E+04
- mrem /yr per,gci/m 3
- 1.87 x 10 6 l
l CLINTON-1 3-103 Rev.5-2/89 l- .
.. ~ . . . ~ - -. . - - - - - -. - . - . _ - - - _ . - . - - - ~ .
TABLE 3.5-22 GOAT MILK PATHWAY FACTORS - Raij C (CHILD)
(m2 mrem /yr per pCi/sec)
ORGAN: EQEE LIVER T . BODY . THYROID KIDNEY LIEQ GI-LLI
.TSOTOPE H-3 NO DATA 3.20E+03* 3.20E+03* 3.20E+03* 3.20E+03* 3.20E+03* 3.20E+03*
C 14 1.65E+06* 3.29E+05* 3.29E+05* 3.29E+05* 3.29E+05* 3.29E+05* 3.29E+05*
-NA 24 1.07E+06** 1.07E+06 1.07E+06 1. 07E+06 1.07E+06 1.07E+06 1.07E+06 P-32. 9.32E+10 4.36E+09 3.59E+09 NO DATA NO DATA NO DATA 2.58E+09 CR 51 NO DATA 'NO DATA 1.22E+04 6.77E+03 . 85E+03 1.24E+04 6.47E+05 MN-54 NO DATA 2.51E+06 6.70E+05 NO DATA 7.05E+05 NO DATA 2.11E+06 MN-56 NO DATA 1.53E-03 '3.45E 04 NO DATA 1.85E-03 NO DATA 2.21E-01 FE 1.45E+06 7.65E+05 2.38E+05 NO DATA NO DATA 4.35E+05 1,42E+05 FE-59 1.55E+06 2.52E+06 1.25E+06 NO DATA NO DATA 7.29E+05 2.62E+06 CO-58 NO DATA 1.46E+06 4.46E+06 NO DATA NO DATA NO DATA 8.49E+06 CO 60 NO DATA 5.16E+06 1.52E+07 NO DATA NO DATA NO DATA 2.86E+07
-NI-63. 3.55E+09 1,90E+08 1.21E+08 NO DATA NO DATA NO DATA 1.28E+07
)
NI-65 1.99E-01 1.87E 02 1. 09E-02 NO DATA NO DATA NO DATA 2.29E+00 CU-64 NO DATA 8.23E+03 4.97E+03 NO DATA 1.99E+04 NO DATA 3.86E+05 ZN-65 4.96E+08 1.32E+09 8.22E+08 NO DATA 8.33E+08 NO DATA 2,32E+08 ZN-69 1. t, / E- 12 1.58E-12 1.46E-13 NO DATA 9.56E-13 NO DATA 9.94E ll BR-83 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA BR 84 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA' BR NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA
-RB-86 NO DATA 1.05E+09 6.47E+08 NO DATA NO DATA NO DATA 6.77E+07 RB-88 NO DATA 8.59E-46 5.97E 46 NO DATA NO DATA NO DATA 4.21E 47 RB-89 NO DATA ' 1 '. 67 E - 5 3 1.49E-53 NO DATA NO DATA NO DATA 1.46E-55 SR 89 1.39E+10 NO DATA 3.96E+08 NO DATA No DATA NO DATA 5.37E+08 SR-90 2.35E+11- NO DATA 5'.95E+10 NO DATA MO DATA NO DATA 3.16E+09 SR-91 2.71E+05 NO DATA 1.02E+04 NO DATA NO-DATA NO DATA 5.99E+05 SR 92 4.61E+00 NO DATA 1.'85 E- 01 NO DATA NO DATA NO DATA 8.74E+01 Y-90 3.86E+01 NO DATA l'.03E+00 NO DATA NO DATA NO DATA 1.10E+05 CLINTON-1 104 Rev.5-2/89 4
. . , , , a r a_ _ -_ - - - - _ _ - -
Gru vuun 1
TABLE-3.5-22 (continued)
C GOAT MILK PATHWAY FACTORS-- R (CHILD) 3 (m2 mrem /yr per pCi/sec) 1 LIVER T. BODY l'HYROID . KIDNEY IEiq GI-LLI ORGAN: HQHE TSOTOPE Y 91m 3.44E-20 NO DATA 1.25E-21 NO DATA NO DATA NO DATA 6.73E-17 Y-91 4.67E+03 NO DATA 1.25E+02 NO Dt.TA NO DATA NO DATA 6.22E+05 Y-92 3.02E 05 NO DATA 8.64E-07 N0* DATA NO DATA NO DATA S.73E-01 Y-93 1.20E 01 N0' DATA 3.29E 03 NO DATA NO DATA NO DATA 1.79E+03 ZR-95 4.58E+02 1.01E+02 8.97E+01 NO DATA 1.44E+02 NO DATA 1.05E+05 ZR-97 2.29E 01 3.31E-02 1,95E-02 NO DATA 4.76E-02 NO DATA 5.02E+03 3.81E+04 1.48E+04 1.06E+04 NO DATA 1.39E+04 NO DATA 2.75E+07
'NB-95 MO-99 NO DATA 9.74E+06 2.41E+06 NO DATA 2.08E+07 NO DATA 8.05E+06 i 1.58E+00 3.10E+00 5.13E+01 NO DATA 4.50E+01 1.57E+00 1.76E+03 TC 99m TC-101 1.54E-60 1.61E-60 2.04E-59 NO CATA 2.74E-59 8.50E 61 5.11E 60 RU-103- 5.10E+02 NO DATA 1.96E+02 NO DATA 1.28E+03 NO DATA 1.32Er04 RU-105 4.53E-04 No DATA 1.65E-04 NO DATA 3.99E 03 NO DATA 2.96E-01 i !
RU-106 1.11E+04 NO DATA 1.38E+03 NO DATA 1.49E+04 NO DATA 1.72E+05 AG-110m 2.50E+07 1.69E+07 1.35E+07 NO DATA 3.15E+07 NO DATA 2.01E+09 8.84E+06 2.39E+06- 1.18E+06 2.48E+06 NO DATA NO DATA 8.53E+06
.TE 125m 2.49E+07 6.71E+06 2.96E+06 5.96E+06 7.10E+07 NO DATA 2.02E+07 TE-127m 3.57E+02 9.61E+01 7.65E+01 2.47E+02 1.01E+03 NO DATA 1.39E+04 TE-127 3.24E+07 9.06E+06 5.03E+06 1.05E+07 9.52E+07 NO DATA 3.96E+07 TE-129m' 1.53E-10 4.28E 11 3.64E-11 1.09E-10 4.49E-10 NO DATA 9.55E-09
.TE-129-1.91E+05 6.60E+04 7.02E+04 1.36E+05 6.39E+05 NO DATA 2.68E+06 TE-131m 1.96E-33 5.97E-34 5.83E-34 1.50E-33 5.92E-33 NO DATA 1.03E-32 TE-131 1
5.45E+05 6.59E+05 7.94E+05 5.06E+06 NO DATA 5.43E+06 TE-132 1.23E+06 4.17E+06 2.15E+06 4.59E+08 6.23E+06 NO DATA 1.95E+C6 I-130 2.06E+06 1.40E+08 1-131 1.56E+09 1.57E+09 8.94E+08 5.20E+11 2.58E+09 NO DATt.
7.03E-01 7.09E+01 2.34E+00 NO DATA 14 80E+00 I-132 8.32E-01 1.52E+00 1.03E+07 1 133 2.06E+07 2.55E+07 9.64E+06 4.73E+09 4.25E+07 NO DATA 1.77E-11 8.13E-12 4.06E-10 2.70E-11 NO DATA 1.17E 11 I-134 9.51E-12 CLINTON-1 3-105 Rev.5 2/89
. , . - , - - - -~ - . . - - .- - . . - - -- .. --
TABLE 3.5-22 (continued)
GOAT MILK PATHWAY FACTORS - R (CHILD)
(m2 mrem /yr per yCi/sec) ggg{; gl{g ' LIVER ' L E D.X 'DIYROID KIDNEY LIREI CI-LLI ISOTOPE 2 135 - 6.53E+04 1.17E+05 5.56E+04- 1.04E+07 1.80E+05 NO DATA 8.95E+04 CS-134 6.76E+10 1.11E+11 2.34E+10 NO DATA 3.44E+10 1.23E+10 5.98E+08 CS-136 3.03E+09 8.33E+09 5.39E+09 h0 DATA 4.44E+09 6.62E+08 2.93E+08 CS 137- 9.65E+10 9.23E+10 1.36E+10 NO DATA 3.01E+10 1.08E+10' 5.78E+08 CS-138 1.15E-22 1.59E-22 1.10E-22 NO DATA 1.12E-22 1.21E 23 7.34E-23 BA-139. 2.42E-08 1.29E-11 7.01E-10 NO DATA 1.13E-11 7.59E 12 1.40E 06 7
BA-140 1.40E+07 1.22E+04 8.15E+05 NO DATA 3.08E+03 7.29E+03 7.07E+06 l BA-141 2.34E-46 1.31E 49 7.62E 48 NO DATA 1.132-49 7.70E 49 1.33E-46 DA-142 1.31E-80 9.44E-84 7.32E-82 NO DATA 7.64E-04 5,55E-84 1.71E 82 1A-140 2.32E+00 8.12E 01 2.53E-01 NO DATA NO DATA NO DATA 2.26E+04
- j. 1A-142 9.85E-12 3.14E 12 9.83E-13 NO DATA NO DATA NO DATA 6.22E 07 L . CE-141 . 2.62E+03 1.31E+03 1.94E+02 NO DATA 5.73E+02 NO DATA 1.63E+06 l-CE-143- 2.24E+01- -1.22E+04 1.76E+00 NO DATA 5.10E+00 NO DATA 1.78E+05 l CE-144 1.94E+05 6.10E+04 1.04E+04 NO DATA 3.38E+04 NO DATA 1.59E+07
, PR-143 8.61E+01 2.58E+01 4.27E+00 NO DATA 1.40E+01 NO DATA 9.20E+04 i i PR-144 3.53E-54 1.09E-54. 1.78E-55 NO DATA 5.78E 55 NO DATA 2.35E 51 ND 147 5.33E+01 4.32E+01 -3.34E+00 NO DATA 2.37E+01 NO DATA 6,84E+04 i- .y-187 3.46E+03 2,05E+03 9.20E+02 NO DATA NO DATA NO DATA 2.88E+05 l
- NP-239- 2.07E+00 1.49E-01 1.04E 01 NO DATA 4.29E-01 NO DATA 1.10E+04 o mrem /yr'per pCi/m 3 O* 1.07 x 10 6 l-l: l l
CLINTON-1 3-106 Rev.6-12/89
,.,me._ _- ,,,.m. -
, , , ~ , - . - . ,v,m...._,..my4, ,,,-..-,-,,.,,,.%.m,-,-.-- -
. CPS-ODCM .
TABLE 3.5-23 ]
GOAT MIII PATHWAY FACTORS - R C (TEEN)
(m2 mrem /yr per sci /sec) i
. ORGAN: M LIVER T. BODY THYT.01D K7DNEY M GI-LLI ISOTOPE j H-3 NO DATA 2.02E+03* 2.02E+03* 2.02E+03* 2.02E+03* 2.02E+03* 2.02+03*
C-14. 6.70E+05* 1.34E+05* 1.34E+05* 1.34E+05* 1.34E+05* 1.34E+05* 1.34E+05*
NA-24 .5.15E+05** 5.15E+05 5.15E+05 5.15E+05 5.15E+05 5.15E+05 5.15E+05 _
P 3.78E+10 2.34E+09 1.47E+09 NO DATA NO DATA NO DATA 3.18E+09 )
CR-51 NO DATA NO DATA 5.94E+03 3.30E+03 1.30E+03 8.48E+03 9.98E+05 MN-54 NO DATA 1.68E+06 3.32E+05 NO DATA 5.00E+05 NO DATA 3.44E+06 1
MN-56 NO DATA 8.77E-04 1.56E-04 NO DATA 1.11E-03 NO DATA 5.77E 02 FE-55 5.79E+05 4.11E+05 9.57E+04 NO DATA NO DATA 2.60E+05 1.78E+05 6.75E+05 1.58E+06 6.08E+05 NO DATA NO DATA 4.97E+05 3.73E+06 FE 59 CO-58 NO DATA 9.51E+05 2.19E+06 NO DATA NO DATA NO DATA 1.31E+07
-CO-60 NO DATA 3.32E+06 7.47E+06 NO DATA NO DATA NO DATA 4.32E+07 ;
NI-63 1.42E+09: 1.00E+08 4.81E+07 NO DATA NO DATA NO DATA 1.60E+07 jl 8.09E-02 1.03E-02 4. 71E 03 NO DATA NO DATA NO DATA 5.61E 01 NI-65 3.63E+05 CU 64 NO DATA 4.6BE+03 2.10E+03 NO DATA 1.18E+04 NO DATA 8.76E+08 4.09E+08 NO DATA 5.61E+08 NO DATA 3.71E+08 ZN-65 2.52E+08 4.44E 13 8.46E-13 5.92E-14 NO DATA 5.53E 13 NO DATA 1.56E 12 ZN-69 NO DATA NO DATA NO DATA NO DATA NO DATA
- BR NO DATA NO. DATA' NO DATA NO DATA NO DATA NO DATA NO DATA BR-84 NO DATA NO DATA NO DATA No DATA NO DATA NO DATA NO DATA BR-85 NO DATA- NO DATA 2.66E+08 NO DATA NO DATA NO DATA 8.38E+07 RB 86 NO-DATA 5.66E+08 4.66E-46 2.48E NO DATA NO. DATA NO DATA 3.99E-53 RB-88 NO DATA 9.52E-54 6.73E-54 NO DATA NO DATA NO DATA 1.46E-62
.RB NO DATA.
1.60E+08 NO DATA NO DATA NO DATA 6.65E+08 SR-89 5.59E+09 NO DATA 3.87E+09 3.40E+10 NO DATA NO DATA NO DATA SR-90. 1.38E+11 'NO DATA 4.40E+03 -NO DATA NO DATA NO DATA 5.01E+05 SR-91 1.11E+05 NO DATA 4,81E+01 8.05E-02 NO DATA NO DATA NO DATA SR 92 1.89E+00 NO DATA NO DATA NO DATA 1.29E+05 Y 90' 1.56E+01 NO DATA 4.21E 01 NO DATA CI,INTON-1 3-107 Rev 5-2/89
' TABLE 3.5-23 (continued)
GOAT MILK PATI!WAY FACTORS - R C (TEEN)
(m2 mrem /yr per yCi/sec)
ORGAN: EqRg LIVER T. BODY THYROID KIDNEY LREI CI-LLI ISOTOPE Y-91m. 1.41E-20 NO DATA 5.37E-22 NO DATA NO DATA NO DATA 6.64E-19 Y-91 1.89E+03 NO DATA 5.07E+01 NO DATA NO DATA NO DATA 7.75E+05 Y 92 1.23E 05 NO DATA 3.57E 07 NO DATA NO DATA NO DATA 3.39E 01 Y 93 4.86E 02 NO CATA 1.33E-03 NO DATA NO DATA NO DATA 1.49E+03 ZR 95 1.98E+02 6.24E+01 4.29E+01 NO DATA 9.17E+01 NO DATA 1.44E+05 ZR-97 9.43E 02 .1.87E 02 8.60E 03 NO DATA 2.83E 02 NO DATA 5.05E+03 NB 95 1.69E+04 9.37E+03 5.16E+03 NO DATA 9.08E+03 NO DATA 4.01E+07 MO 99 NO DATA 5.33E+06 1.02E+06 NO DATA 1.22E+07 NO DATA 9.55E+06 TC-99m 6.87E-01 1.92E+00 2.48E+01- NO DATA 2.86E+01 1.06E+00 1.26E+03 TC 101 6,26E-61 0.91E 61 8.75E-60 NO DATA 1.61E-59 5.43E 61 1.52E-67 RU 103 2.17E+02 NO DATA 9.27E+01 NO DATA 7.64E+02 NO DATA 1.81E+04 RU-105 1.86E 04 NO DATA 7.21E 05 NG OATA 2.35E-03 NO DATA 1.50E-01 RU-106 4.47E+03 NO DATA
- 63E+02
. NO DATA 8.62E+03 NO DATA 2.14E+05 A0-110m. 1.15E+07 1.09E+07 6.62E+06 NO DATA 2.08F+07 NO DATA 3.06E+09 TE-125m 3.59E+06 1.29E+06 4.80E+05 1.00E+06 NO DATA NO DATA 1.06E+07 TE-127m 1.01E+07 3.57E+06 1.20E+06 2.39E+06 4.08E+07 .NO DATA 2.51E+07 TE-127' 1.48E+02 5.14E+01 3.18E+01 1.02E+02 5,87E+02 NO DATA 1.14E+04 TE 129m 1.32E+07 4.89E+06 2.08E+06 4.25E+06 5.51E+07 NO DATA 4.94E+07
-(
TE 129 6.22E-11 2.32E-11. 1.51E 11 4.44E 2.61E 10 NO DATA 3.40E 10 TE-131m 7.86E+04 3.77E+04 3.14E+04 5.67E+04 3.93E+05 NO DATA 3.02E+06 TE-131' 8.04E-34 3.31E-34 2.b1E 34 6.19E-34 3.51E-33 NO DATA 6.60E-35 TE-132 5.13E+05 3.25E+05 3.06E+05 3.43E+05 3.12E+06 NO DATA 1.03E+07
-I-130 8.82E+05 2.55E+06 1.02E+06 2.08E+08 3.93E+06 NO DATA 1.96E+06 I-131 6.44E+0C 9.01E+08 4.84E+08 2.63E+11 1.55E+09 NO DATA 1.78E+08 I-132. 3,52E-01 9.70E-01 3.30E-01 3.10E+01 1.45E+00 NO DATA 4.01E-01 I-133 8.48E+06 1.44E+07 4.39E+06 2.01E+09 2.52E+07 NO DATA 1.09E+07 I-134 4.03E 12 1.07E-11 3.84E-12 1.78E-10 1.68E-11 NO DATA 1.41E-13 CLINTON-1 3-108 Rev.5-2/89 e
. - - -- . . -- ~ . ~ = .. . .. -
CPS-ODCM TABLE 3.5-23 (continued)
C
. GOAT MIII PATHWAY _ FACTORS - R (TEEN)
(m2 mrem /yr per pCi/sec)
ORGAN! fjQF_E LIVER T. BODY THYROID KIDNEY LIR{G Q.I-LLI 2.62E+04 4.56E+06 1.12E+05 NO DATA 7.85E+04 I 135 2.75E+04 7.08E+04 8,60E+08 2.94E+10 6.91E+10 3.21E+10 NO DATA 2.20E+10 8.39E+09 CS 134 4.24E+08 CS-136 1.34E+09 5.27E+09 3.54E+09 NO DATA 2.87E+09 4.52E+08 1.86E+10 NO DATA 1.82E+10 7.05E+09 7.59E+08 CS-137 4.01E+10 5.33E+10 9.08E-23 4.54E 23 NO DATA 6.70E 23 7.80E 24 4.12E-26 CS-138. 4.73E-23 8.78E-08 9.84E 09 6.92E-12 2.87E-10 NO DATA 6,53E-12 4.77E-12 BA-139 ,
3.75E+05 NO DATA
- 2.42E+03 4.80E+03 8.98E+06 BA-140 5.82E+06 7.13E+03 3.18E-48 NO DATA 6.60E-50 4.87E-50 2.03E 52 BA 141 9.53E 47 7.11E-50 5.44E 84 3.35E-82 NO DATA 4.60E-84 3.62E-84 1.67E-92 BA-142 5.44E-81 1.26E 01 NO DATA NO LATA NO DATA 2.73E+04 LA 140 9.67E-01 4. 7'J E-01 1.81E-12 4.51E-13 NO DATA NO DATA NO DATA 5.52E 08 LA-142 4.08E-12 2.04E+06 7.12E+02 8.17E+01 NO DATA 3.35E+02 NO DATA )
CE-141 1.07E+03 7.43E 01 NO DATA 2.98E+00 NO DATA 2.00E+05 CE 143 9.14E+00. -6.65E+03 1.98E+07 3.25E+04 4.23E+0! NO DATA 1.94E+04 NO DATA CE-144 7.86E+04 1.73E+00 NO DATA 8.06E+00 NO DATA 1.14E+05 PR-143 3.47E+01 1.39E+01 5.81E-55 7.19E-56 NO DATA 3.33E-55 NO DATA 1.56E-57 PR-144 1.42E-54 8.50E+04 2.17 E+0L 2.36E+01 1.41E+00 NO DATA 1.38E+01 NO DATA ND-147 1.16E+03 4.08E+02 NO DATA NO DATA NO-DATA 3.15E+05 f -- 'J- 187 1.43E+03 7.90E-02 4.39E-02 NO DATA 2.48E-01 NO DATA 1.27E+04 NP-239 8.38E-01 t
l 3
l
- mrem /yr per pCi/m
- 5.15 x 10 5' i'
1 CLINTON-1 3-109 Rev.5-2/89 9
. - . . - - - ~ - . . --. - - . ~ . - . ._ .
TABLE-3.5-24
' GOAT MILK PATHWAY FACTORS -
RC (ADULT)
(m2 mrem /yr per pci/sec) $
ORGAN: HQF.X LIVER T. BODY THYROID KIDNEY LIMG CI-LLI YSOTOPE H3 NO DATA 1.55E+03* 1.55E+03* 1.55E+03* 1.55E+03* 1.55E+03* 1.55E+03*
C-14 3.63E+05* 7.26E+04* 7.26E+04* 7.26E+04* 7.26E+04* 7.26E+04* 7.26E+04*
NA 24 - 2.95E+05** 2.95E+05 2.95E+05 2.95E+05 2.95E+05 2.95E+05 2.95E+05 P-32 2.05E+10 1.27E+09 7.91E+08 NO DATA NO DATA NO DATA 2.30E+09 CF.-51 NO-DATA NO DATA 3.43E+03 2.05E+03 7.56E+02 4.55E+03 8.63E+05 MN-54 NO DATA 1.01E+06 1.92E+05 NO DATA 2.99E+05 NO DATA 3.08E+06 MN 56 NO DATA 4.96E-04 8.79E-05 NO DATA 6.29E 04 NO DATA 1.58E 02 FE 55 3.27E+05 2.26E+05 5.27E+04 NO DATA NO DATA 1.26E+05 1.30E+C5 FE-59 3.85E+05 9.06E+05 3.47E+05 NO DATA NO DATA 2.53E+05 3.02E+06 CO-58 NO DATA 5.62E+05 1.26E+06 NO DATA NO DATA NO DATA '.14E+07 CO-60 NO DATA 1.96E+06 4.33E+06 NO DATA NO DATA NO DATA . 69E+07 NI-63 8.05E+08 5.58E+07 2.70E+07 NO DATA NO DATA NO DATA 1.16E+07
).
NI 65 4.43E-02 5.76E 03 -2.63E-03 NO DATA NO DATA NO DATA 1.46E-01 CU 6A NO DATA 2.62E+03 1.23E+03 NO DATA 6.62E+03 NO DATA 2.24E+05 ZN-65 1.64E+08 5.22E+08 2.36E+08 NO DATA 3.49E+08 NO DATA 3.29E+08 2.N- 69 2.41E-13 4.61E-13 '.21E-14
. NO DATA 3.00F. 13 NO DATA 6.93E-14 BR-83 - NO DATA NO DATA MO DATA NO DATA NO DATA NO DATA NO DATA BR 84 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA BR-85 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA RB 86 NO DATA 3.10E+08 1.45E+08 NO DATA NO DATA NO DATA 6.12E+07 RB-88 NO DATA 2.57E-46 1.36E 46 NO DATA NO DATA NO DATA 3.55E-57
-RB-89 NO DATA 5.37E-54 3.78E-54 NO DATA- NO DATA NO DATA 3.12E-67 SR-89 3.04E+09 NO DATA 8.73E+07 NO DATA NO DATA NO DATA 4.88E+08 SR-90 9.78E+10 NO DATA 2.40E+10 NO DATA NO DATA NO DATA 2.83E+09 SR-91 6.01E+04 NO DATA 2.43E+03 NO DATA NO DATA NO DATA 2.86E+05 SR-92 1.03E+00 NO DATA 4.45E-02 NO DATA NO DATA NO DATA 2.04E+01 Y-90 8.48E+00 NO DATA 2,28E-01 NO DATA NO DATA NO DATA 9.00E+04 CLINTON-1 3-110 Rev.5-2/89 p'4--' 1,- v8 m- gs w,- g+-., n - see-.-, - , . _
. CPS-ODCM TABLE 3.5-24 (continued)
GOAT MILK PATHWAY FACTORS - R (ADULT)
(m2 mrem /yr per pCi/ soc)
ORCAN! SQllE LIVER T. BODY THYROID KIDNEY LWQ 9I-LLI ISOTOPE Y-91m 7.69E-21 NO DATA 2.98E-22 NO DATA NO DATA NO DATA 2.26E-20 1.03E+03 NO DATA 2.75E+01 NO DATA NO DATA NO DATA 5.66E+05 Y-91 1.17E 01 Y-92 6.68E-06 NO DATA 1.95E-07 NO DATA NO DATA NO DATA Y-93 2.65E-02 NO DATA 7.32E 04 NO DATA NO DATA NO DATA 8.41E+02 3
ZR-95 1.13E+02 3.63E+01 2.46E+01 NO DATA 5.69E+01 NO DATA 1.15E+05 ZR-97 5.17E-02 1.04E-02 4.77E-03 NO DATA 1.58E-02 NO. DATA 3.23E+03 NB-95 9.90E+03 5.51E+03 2.96E+03 NO DATA 5.45E+03 NO DATA 3.34E+07 MO-99 NO DATA 2.96E+06 5.63E+05 NO DATA 6.71E+06 NO DATA 6.86E+06 3.95E-01 1.12E+00 1.42E+01 NO DATA 1.70E+01 5.47E-01 6.61E+02 T0-99m TC-101 3.43E-61 4.94E-61 4.84E-60 NO DATA 8.89E-60 2.52E-61 1.48E-72 RU-103 1.22E+02 NO DATA 5.24E+01 NO DATA 4.64E+02 NO DATA 1.42E+04 RU-10.5 1.02E-04 NO DATA 4,02E-05 NO DATA 1.32E-03 NO DATA 6.23E-02
)
RU-106 2.44E+03 NO DATA 3.09E+02 NO DATA 4.72E+03 NO DATA 1.58E+05 AG-110m 6.96E+06 6.44E+06 3,82E+06' NO DATA 1.27E+07 NO DATA 2.63E+09 TE-125m- 1.95E+06 7.07E+05 2.61E+05 5.87E+05 7.94E+06 NO DATA 7.79E+06 TE-127m 5.46E+06 1.95E+06 6.66E+05 1.40E+05 2.22E+07 NO DATA 1.83E+07 7.82E+01 2.81E+01 1.69E+01 5.80E+01 3.19E+02 NO DATA 6.17E+03 TE-127 TE 129m 7.21E+06 2.69E+06 1.14E+06 2.48E+06 3.01E+07 NO DATA 3.63E+07 TE 129 3.83E-11 1.27E 11 8.23E-12 2.59E-11 1.42E-10 NO DATA 2.55E 11 TE-131m_ 4.33E+04 2.12E+04 1.76E+04 3.35E+04 2.14E+05 NO DATA 2.10E+06 TE-131 4.37E-34 1.83E-34 1.38E-34 3.60E-34 -1.92E-33 NO DATA 6.19E-35' TE-132 2.87E+05 1.86E+05 1.74E+05 2.05E+05 1.79E+06 NO DATA 8.79E+06 I-130 5.00E+05 1.47E+06 5.82E+05 1.25E+08 2.30E+06 NO DATA 1.27E+06 1-131 3.54E+08 5.06E+08 2.90E+08 1.66E+11 8.68E+08 NO DATA 1.34E+08 I-132 1.98E-01 5.29E-01 1.85E-01 1.85EF01 8.43E-01 NO DATA 9.93E 02 I-133 4.62E+06 8.03E+06 2.45E+06 1.18E+09 1.40E+07 NO DATA- 7.22E+06 1 134- 2.27E-12 6.16E-12 2.20E-12 1.07E-10 9.80E-12 NO DATA S.37E-15 CLINTON-1 3-111 Rev.5-2/89 t -- --v-- - -
. . - _ . _ _._ . . . - . . _ . _ _ . _ _ _ . _ . . _ = .
urs-uvun .
TABLE 3.5-24 (continued)
GOAT MILK PATHWAY FACTORS - R C (ADULT)
(m2 mrem /yr per yCi/sec)
ORGAN: IQHE LIVER T. BODY THYROID KIDNEY LELQ GI-LLI ISOTOPE I-135 1.55E+04 4.06E+04 1.50E+04 2.68E+06 6.51E+04 NO DATA 4.59E+04 CS-134 1.69E+10 4.03E+10 3.29E+10 NO DATA 1.30E+10 4.32E+09 7.04E+08 '
CS-136 7.88E+08 3.11E+09 2.24E+09 NO DATA 1.73E+09 2.37E+08 3.53E+08 CS-137 2.21E+10 3.03E+10 1.98E+10 NO DATA 1.02E+10 3.41E+09 5.84E+08 CS-138 2.61E-23 5.15E-23 2.55E-23 NO DATA 3.78E-23 3.73E-24 2.20E-28 BA-139 5.32E-09 3.79E-12 1.56E-10 NO DATA 3. 54 E- 12 2.15E 12 9.44E-09 BA-140 3.23E+06_ 4.05E+03 ,2.11E+05 NO DATA 1.38E+03 2.32E+03 6.65E+06 BA-141- 5.18E 47 3.92E.50 1.75E 48 NO DAEA 3.64E-50 2.22E-50 2.44E 56 BA 142 3.00E-81 3.09E 84 1.89E 82 NO DATA 2.61E-84 1.75E-84 4.23E-99
-LA-140 5.40E-01 2.72E-01 7.19E 02 NO DATA NO DATA NO DATA 2.00E+04 LA-142 .2.27E-12 1.03E-12 2,57E-13 NO DATA NO DATA NO DATA 7.52E-09 CE 141' 5.80E+02. 3.92E+02 4.45E+01 NO DATA 1.32E+02 NO DATA 1.50E+06 i
CEd 3 5.00E+00 3.70E+03 4.09E-01 NO DATA 1.63E+00 NO DATA 1.38E+05 CE-14' 4.29E+04 1.79E+04 2.30E+03 NO DATA 1.06E+04 NO DATA 1.45E+07
'PR-141 1.80E+01 7.56F+00 9.35E-01 NO DATA 4,37E+00 .NO DATA 8.26E+04 PR 144 7.71E-55 3.20E-55 3.92E-56 NO DATA 1.80E-55 NO DATA 1.11E-61 N' '7 1.13E+01 1.30E+01 7.79E-01 NO DATA 7.64E+00 NO DATA 6.25E+04 V -1 ~7.78E+02 6.50E+02 2.27E+02 NO DATA NO DATA NO DATA 2.13E+05 NP-239 4.39E-01 4.32E-02 2.38E 02 NO DATA 1.35E-01 NO DATA 8.86E+03
- mrem /yr per pCi/m 3 O* 2.95'x 105 CLINTON-1 3-112 Rev.5-2/89
. . ~ . . . -.
-CVu~uuen t TABLE 3.5-25 MEAT PATHWAY FACTORS - R (CHILD) )
(m2 mrem /yr per pCi/sec)
THYROID KIDNEY LELG GI-LLI QRGAN: 10E LIVER T. BODY ISOTOPE H3 NO DATA 2.33E+02* 2.33E+02* 2.33E+02* 2.33E+02* 2.33E+02* 2.33E+02*
C-14 5.29E+05* 1.06E+05* 1.06E+05* 1.06E+05* 1.06E+05* 1.06E+05 1.06E+05*
-NA-24 .l.84E-03** 1.84E-03 1.84E-03 1.84E-03 1.84E-03 1.84E-03 1.84E 03 P-32 7.43E+09 3.47E+08 2.86E+08 NO DATA NO DATA NO DATA 2.05E+08 CR-51 NO DATA NO DATA 8.78E+03 4.88E+03 1.33E+03 8.90E+03 4.66E+05 MN-54 NO DATA 8.03E+06 2.14E+06 NO DATA 2.25E+06 NO DATA 6.74E+06 MN-56 NO DATA 1.56E-53 3.52E-54 NO DATA 1.89E-53 NO DATA 2.26E 51 FE-55 4.58E+08 2.43E+08 7.52E+07 NO DATA NO DATA 1.37E+08 4.50E+07
-FE-59 3.76E+08 6.09E+08 3.03E+08 NO DATA NO DATA 1.76E+08 6.34E+08 CO 58 NO DATA- 1.64E+07 5.03E+07 NO DATA NO DATA NO DATA 9.58E+07 CO-60 NO DATA 6.93E+07 2.04E+08 NO DATA NO DATA NO DATA 3.84E+08 NI-63 2.91E+10 1.56E+09 9.90E+08 NO DATA NO DATA NO DATA 1.05E+08 i
NZ-65 3.55E-52 3,34E-53 1.92E-53 NO DATA NO DATA NO DATA 4.10E-51
-CU-64 NO-DATA 2,77E-07 1.67E 07 NO DATA 6.69E-07 NO DATA 1.30E-05 ZN-65 3.75E+08 1.00E+09 6.22E+08 do DATA 6.30E+08 NO DATA 1.76E+08 ZN-69 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 NO DATA 0.00E+00 NO DATA NO' DATA NO DATA NO DATA NO DATA NO DATA BR-83 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA BR-84 NO DATA BR-85 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA RD-86 NO DATA 5.76E+08 3.54E+08 NO DATA NO DATA NO DATA 3.71E+07 RB-88 NO DATA 0.00E+00 0.00E+00 NO DATA- ~ NO DATA NO DATA 0.00E+00 RB-89 NO DATA 0.00E+00 0.00E+00 NO DATA NO DATA NO DATA 0.00E+00
~SR-89 4.80E+08 NO DATA 1.37E+07 NO DATA NO DATA NO DATA 1.86E+07 SR-90 1 04E+10 NO DATA 2.64E+09 NO DATA NO DATA NO DATA 1.40E+08 SR 91 2.26E-10 N0' DATA 8.53E-12 NO DATA NO DATA NO DATA 4.99E-10 SR-92 2.00E-49 NO DATA 8.04E-51 NO DATA NO DATA NO DATA 3.80E-48 Y-90 1.73E+02 - NO DATA 4.62E+00 NO DATA NO DATA NO DATA 4.91E+05 CLINTON-1 3-117 Rev 5-2/89
TABLE 3.5-25 (continued) i MEAT PATHWAY FACTORS - R (CHILD) .
(m2 mrem /yr per pCi/sec)
ORGAN;. Epf.E LIVER T. BODY THYROID _ KIDNEY lyEQ. GI-LLI ISOTOPE Y-91m 0.00E+00 NO DATA 0.00E+00 NO DATA NO DATA NO DATA 0.00E+00 Y 91 1.80E+06 NO DATA 4.81E+04 NO DATA NO DATA NO DATA 2.40E+08 Y-92 2.37E-39 NO DATA 6.78E 41 NO DATA NO DATA NO DATA 6.84E-35
-Y-93 6.98E NO DATA 1.92E-13 NO DATA NO DATA NO DATA 1.04E-07
.ZR 95 - 2.67E+06 5.87E+05 5.22E+05 NO DATA 8.40E+05 NO DATA 6.12E+08 ZR 97 3.16E-05 4.57E 06 2.69E 06 NO DATA 6.55E-06 NO DATA 6.92E 01 NB 95 3.10E+06 1.21E+06 8.61E+05 NO DATA 1.13E+06 NO DATA 2.23E+09 MO 99 NO DATA 1.14E+05 2.83E+04 NO DATA 2.44E+05 NO DATA 9.45E+04 TC-99m ' 6.01E 21 1.18E-20 1.95E-19 NO DATA 1 71E-19 5.98E-21 6.71E 18 TC 101 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 0.00E+00 0.00E+00 RU 103 1.55E+08 NO DATA 5.96E+07 NO DATA 3.90E+08 NO DATA 4.01E+09 RU-105 8.48E-28 NO DATA 3.08E-28 NO DATA 7.45E-27 NO DATA 5.54E-25
)
RU 106 4.43E+09 NO DATA 5.53E+08 NO DATA 5.99E+09 NO DATA 6.90E+10 AC-110m 8.41E+06 5.68E+06 4.54E+06 NO DATA 1.06E+07 NO DATA 6 '. 75 E+0 8 TE 125m 5.69E+08 1.54E+08 7.58E+07 1.60E+08 NO DATA NO DATA 5.49E+08 TE-127m 1.77E+09 4.78E+08 2.11E+08 -4.24E+08 5.06E+09 NO DATA 1.44E+09 TE-127 3.34E 10 9.01E-11 '7.17E-11 2.31E-10 9.51E 10 NO DATA 1.31E-08 TE 129m 1.79E+09 4.99E+08 2.77Ee08 5.76E+08 5.25E+09 NO DATA 2.18E+09 TE-129 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0,00E+00 NO DATA 0.00E+00 TE 131m 6.97E+02 2.41E+02 2.57E+02 4.96E+02 -2,33E+03 NO DATA 9.78E+03
<TE-131 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00
.TE-132 2.13E+06 9,43E+05 1.14E+06 1.37E+06 8.76E+06 NO DATA 9.50E+06 I-130 2.91E-06 5.89E 06- 3.03E 06 6.49E-04 8.80E-06 NO DATA -2.75E-06 I-131 1.65E+07 1.66E+07 9.46E+06 5.50E+09 2.73E+07 NO DATA 1.48E+06 I-132 1.05E-58 1.93E-58 8.86E-59 8.93E 57 2.95E-58 - NO DATA 2.27E-58 I-133 . 5.75E-01 7.10E-01 2.69E-01 1.32E+02 1.18E+00 NO DATA 2.86E 01 I-134 0.00E+00 0.00E+00 0. 00E4 00 0.00E+00 0.00E+00 NO DATA 0.00E+00 CLINTON-1 3-114 Rev.5-2/89
. . = . _ . __- . _ ._
CPS 0DCn-TABLE 3.5-25 (continued)
MEAT PATHWAY FACTORS - RMai-j (CHILD) )
(m2 mrem /yr per pCi/sec) ,
QRGAN:. AQEE LIVER T. BODY THYROID KIDNEY lE!Q GI.LLI YSOTOPE I-135 6.86E-17 1.23E-16 5.83E-17 1.09E 14 1.89E-16 NO DATA 9.38E-17 CS-134 9.20E+08 1.51E+09 3.18E+08 NO DATA 4.68E+08 1.68E+08 8.14E+06 CS 136 1.62E+07 4.45E+07 2.88E+07 NO DATA 2.37E+07 3.53E+06 1.56E+06 CS 137 1.33E+09 1.27E+09 1. 88E448 NO DATA 4.15E+08 1.49E>08 7.98E+06 CS 138 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 0.00E+00 0.00E+00 9A-139 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 0.00E+00 0.00E+00
?BA-140 4.38E+07 3.8AE+04 2.56E+06- NO DATA 1.25E+04 2.29E+04 2.22E+07 BA-141 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 0.00E+00 0.00E+00 BA-142 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 0.00E+00 0.00E+00 LA-140 5.56E-02 1.94E-02 6.05E 03 NO DATA NO DATA NO DATA 5.41E+02 1A-142 6.18E-92 1.97E 92 -6.17E 93 NO DATA NO DATA NO DATA 3.91E.87 ;
2.22E+04 1.11E+04 1.64E+03 NO DATA 4.85E+03 NO DATA 1.38E+07 CE-141 CE-143 3,20E 02 1.74E+01 2.51E-03. NO DATA 7.28E-03 NO DATA 2.54E+02 CE-144 2.31E+06- 7.24E+05 1.23E+05 NO DATA 4.01E+05 NO DATA 1.89E+08 3.34E+04 1.00E+04 1.66E+03 NO DATA 5.43E+03 NO DATA 3.60E+07 PR-143 PR-144 0.00E+00 0.00E+00 0.00E+00 NO DATA -0.00E+00 NO DATA 0.00E+00 1.17E+04 9.47E+03 7.33E+02. NO DATA .5.20E+03 NO DATA 1.50E+07 ND-147 W-187 3.21E-02 '1.90E-02 3.53E-03 NO DATA NO DATA NO DATA 2.67E+00 4.23E-01 3.04E-02 2.14E-02 NO DATA 8.79E NO DATA 2.25E+03 WP 239 l
- mrem /yr per pCi/m3
- ** '1 84-x 10-3 i-l CLINTON-1 3-115 Rev.6-12/89 l
-TABLE 3.5-26 MEAT PATHWAY FACTORS - R (TEEN) i (m2 mrem /yr per pCi/sec)
ORGAN
- AQE LIVER T. BODY THYROID KIDNEY L12Hg, GI-LLI ISOTOPE H 3- NO DATA 1.93E+02* 1.93E+02* 1.93E+02* 1.93E+02* 1.93E+02* 1.93+02*
C-14 2.81E+0$* 5,62E+04* 5.62E+04* 5.62E+04* 5.62E+04* 5.62E+04* 5.62E+04*
NA-24 1.16E 03** 1.16E 03 1.16E-03' 1.16E-03 1.16E-03 1.16E 03 1.16E-03 P 32 3.95E+09 2.45E+08 1.53E+08 NO DATA NO DATA NO DATA 3.32E+08 CR-51 NO DATA NO DATA 5.65E+03 3.14E+03 1.24E+03 8.07E+03 9.50E+05 MN-54 NO DATA 7.02E+06 1.39E+06 NO DATA 2.09E+06 NO DATA 1.44E+07 MN-56 NO DATA 1.17E-53 2.09E-54 NO DATA 1.48E-53 NO DATA 7.72E 52 FE-55 2.38E+08 1.69E+08 3,94E+07 NO DATA NO DATA 1.07E+08 7.31E+07 FE 59 2.12E+08 4.95E+08 1.91E+08 NO DATA NO DATA 1.56E+08 1.17E+09 CO 58 NO-DATA 1.41E+07 3.2SE+07 NO DATA NO DATA NO DATA 1.94E+08 CO-60 - NO DATA 5.84E+07 1.32E+08 NO DATA NO DATA NO DATA 7.61E+08 1.52E+10 1.07E+09 5.15E+08 NO DATA NO DATA. NO DATA 1.71E+08
)NI-63 NI-65 - 1.90E 52 2.43E 53 1.11E 53 NO DATA No DATA NO DATA 1.32E-51 CU 64 NO DATA 2.06E-07 9.68E-08 NO DATA 5.21E-07 NO DATA 1.60E-05 ZN 65 2.50E+08 8.69E+08 4.0$E+08 NO DATA 5.56E+08 NO DATA 3.68E+08 ZN-69 - 0.00E+00 0.00E400 0.00E+00 NO DATA 0.00E+00 NO DATA 0.00E+00 BR-83 NO DATA. NO-DATA NO DATA -NO DATA NO DATA NO DATA NO DATA BR-84 NO DATA NO DATA- NO DATA NO DATA NO DATA NO DATA NO DATA BR-85 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA RB-86 NC DATA ~ 4.05E+08 1,90E+08 NO DATA NO DATA NO DATA 6.00E+07 RB-88. NO DATA 0.00E+00 0,00E+00- NO DATA NO DATA NO DATA 0.00E+00 RB 89 NO DATA- 0.00E+00 0.00E+00 NO DATA NO DATA NO DATA 0.00E+00 SR 2.54E+08 NO DATA 7.27E+06 NO DATA NO DATA NO-DATA 3. 02 E+ 07 SR-90 8.04E+09 NO DATA 1.99E+09 NO DATA NO DATA NO DATA 2.26E+08 4
SR 1.20E-10 NO DATA 4.-78E-12 NO DATA NO DATA NO DATA 5.45E-10 SR 92 1.08E-49 NO DATA 4.59E-51 NO DATA NO DATA NO DATA 2.74E-48 Y-90 9.11E+01 NO DATA 2.45E+00 NO DATA NO DATA NO DATA 7.51E+05 l
l CLINTON-1 3-116 Rev.5-2/S9 l
.- r_
4 4 I
TABLE 3.5-26 (continued)
MEAT PATHWAY FACTORS - R (TEEN)
(m2 mrem /yr per pCi/sec)
,B9.HE LIVER T. BODY THYROID KIDNEY jdEG GI-LLI QRGAN:
Is0 TOPE Y-91m 0.00F,+00 NO DATA ~ 0.00E+00 NO DATA NO DATA NO DATA 0.00E+00 3.91E+08 Y-91' 9.55605 NO DATA 2.56E+04 NO DATA NO DATA NO DATA Y 92 1.26E 39 NO DATA 3.64E 41 NO DATA NO DATA NO DATA 3.45E-35 Y-93 3.70E-12 NO DATA 1.01E-13 NO DATA NO DATA NO DATA 1.135-07 ZR 95 1.50E+06 4.74E+05 3.25E+05 NO-DATA 6.93E+05 NO DATA 1.09E+09 ZR 1.70E-05 3.36E-06 1.55E 06 NO DATA 5.10E 06 NO DATA 9.11E 01
. _. =
NB-95 1.79E+06 9.94E+05 5.47E+05 NO DATA 9.64E+05 NO DATA 4.25E+09 MO-99 NO DATA 8.20E+04 1.56E+04 NO DATA 1.88E+05 NO DATA 1.47E+05 TC-99m 3.42E-21 9.54E-21 1.24E-19 NO DATA 1.42E-19 5.29E 21 6.2dE-18 TC-101 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 0.00E+00 0.00E+00 RU-103 8.57E+07- NO DATA 3.66E+07 NO DATA 3.02E+08 NO DATA 7.16E+09 RU-105 4.56E-28 NO DATA 1.77E-28 NO DATA 5.75E-27 NO DATA 3.68E-25 i;
2.36E+09 NO DATA 2.97E+08 NO DATA 4.54E+09 NO DATA 1.13E+11 RU-106 AG-110m .5.04E+06 4.77E+06 2.90E+06 NO DATA 9.10E+06 NO DATA 1.34E+09 3.03E+08 1.09E+08 4.06E+07 8,47Et C NO DATA NO DATA 8.95E+08 TE-125m 9.40E+08 3.33E+08 1.12E+08 2.24E+08 3.81E+09 NO DATA 2.34E+09 TE-127m
- TE 127 1.78E-10 6.30E 11 3.82E-11 1.23E-10 7.20E-10 NO DATA 1.37E-08 9.49E+08 3.52E+08 1.50E+08 3.06E+08 3.97E+09 NO DATA 3.56E+09 TE 129m 0.00E+00 0.00E+00 0.00E 00 0.00E+00 NO DATA 0.COE-r00 TF-129 0.00E+00 3.73E+02 1.79E+02 1.49E+02 2.69E $2 1.87E+03 NO DATA 1.44E+04 TE-131m 0.00E+00 0.00EF00 0.00E+00 0.00E+v0 0.00E+00 NO DATA 0.00E+00 TE 131 1.17E+06 7.38E+05 6.95E+05 7.78E+05 7.08E+06 NO DATA 2.34E+07
. TE 132 I-130 1.63E-06 4.71E-06 1.88E-06 3.84E-04 7.25E-06 NO DATA 3.62E-06
- I 131 8.89E+06 1.24E+07 6.69E+06 3.63E+09 2.14E+07 NO DATA 2.46E+06 1.51E-58 5.42E 59 5.09E 57 2.38E-58 NO DATA 6.58E-59 I-132 5.78E 59 3.97E-01 I-133- 3.09E-01 5.25E-01 1.60E 01 7.32Er01 9.20E+01 NO DATA L 0.00r+00 I 134 0.00E+0C 0.00E+00 0.00E+00 0.00E+00 0.00E+00 NO DATA i
CLINTON-1 3 117 Rev.5-2/89
l TABLE 3.5-26 (continued)
MEAT PATHWAY FACTORS - R (TEEN)
(m2 mrom/yr per pci/sec)
ORGAfD EQE LIVER .T. BODY THYROID KIDNEY LlEQ GI LLI
.UpTOPE
- I-135 3.79E 17 9.75E-17 3.61E-17 6.27E 15 1.54E 16 NO DATA 1,08E-16 CS-134 5.22E+08 1.23E+09 5.70E+08 NO DATA 3.91E+08 1.49E+08 1.53E+07
.CS 136 9.36E+06 3.68E+07 2.47E+07 NO DATA 2.01E+07 3.16E+06 2.96E+06 CS-137~ 7.24E+08 9.63E+08 3.35E+08 NO DATA 3.28E+08 1.27E+08 1.37E+07 CS-138 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 0.00E+00 0.00E+00 BA-139 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 0.00E+00 0.00E+00 BA-140 2.37E+07 2.91E+04 1.53E+06 NO DATA 9.86E+03 1.96E+04 3.66E+07 BA-141 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 0.00E+00 0.00E+00 BA-142 0.00E+00 0.00E+00 0.00E+00- NO DATA 0.00E+00 0.00E+00 0.00E+00 LA 140 3.03E 02 1.49.' 02 3.97E-03 NO DATA NO DATA NO DATA 8.56E+02 LA 142 3.37E-92 1.49E 92 3.72E-93 NO DATA NO DATA NO DATA 4.55E-88 CE-141 1.17E+04 7.83E+03 9.00E+02 NO DATA 3.69E+03 NO DATA 2.24E+07
)
CE-143 1.70E-02 1.24E+01 1.38E-03 .NO DATA 5.55E 03 NO DATA 3.72E+02 CE-144 1.23E+06 5.10E+05 6.62E+04 NO DATA 3.C'E+05 NO DATA 3.10E+08 PR 143 1.77E+04 7.06E+03 8.80E+02 NO DATA 4.10E+03 NO DATA 5.82E+07
.PR-144 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 NO DATA 0.00E+00 ND 147 6.'22E+03 6.76E+03 4.05E+02 NO DATA 3.97E+03 NO DATA 2.44E+07 W-187 :1.74E 02 1.42E 02 4,96E-03 NO DATA NO DATA MO DATA- 3.83E+00 NP 239 2.25E-01 2.12E 02 1.18E 02 NO DATA 6.67E-02 NO DATA 3.42E+03
- mrem /yr per pCi/m 3
- 1.16 x 10-3 l
CLINTON-1 3-118 Rev.5-2/89
1 CPS 0DCM-TABLE 3.5-27 MEAT PATHWAY FACTORS - R (ADULT)
(m2 mrom/yr per pCi/sec) !
ORGAN: ggy_g Lly.' T. BODY THYROID KIDNEY lja!f GI-LLI ISOTOPE l H-3 NO DATA 3.24E+02* 3.24E+02* 3.24E+02* 3.24E+02* 3.24E+02* 3.24E+02* '
0-14 3.33E+05* 6.66E+04* 6.66E+04* 6.66E+04* 6.66E+04* 6.66E+04* 6.66E+04*
NA 24 1.45E-02** 1.45E-03 1.45E 03 1.45E-03 1.45E-03 1.45E 03 1.45E 03 ]
i F-32 4.65E+09 2.89E+08 1.80E+08 NO DATA NO DATA NO DATA 5.23E+08 CR-51 NO DATA NO DATA 7.05E+03 4.21E+03 1.55E+03 9.35E+03 1.77E+06 i MN-54 NO DATA 9.19E+06' 1.75E+06 NO DATA 2.73E+06 NO DATA 2.81E+07 MN 56 NO DATA 1.45E-53 2.57E-54 NO DATA 1.84E-53 NO DATA 4.62E-52 i FE-55 2.94E+08 2.03E+08 4.74E+07 NO DATA NO DATA .13E+08 1.17E+08 FE 59 2.66E+08 6 24E+08 2.39E+08 NO DATA NO DATt 1.74E+08 2.08E+09 CO-58 NO DATA 1.83E+07 4.09E+07 NO DATA NO DATA NO DATA 3.70EA08 CO 60 NO DATA 7,51E+07 1.66E+08 NO DATA NO DATA NO DATA- 1.41E+09 HI-63 1.89E+10 1.31E+09 6.32E+08 NO DATA NO DATA NO DATA 2.73E+08 i'
NI-65 2.27E-52 2.94E-53 1.34E-53 NO DATA NO DATA NO DATA 7.46E-52 CU-64 NO DATA 2.52E-07 1.18E-07 NO DATA 6.36E-07 NO DATA 2.15E 05 J7.N-65 3.56Evo8 1.13E+09 5.12E+08 NO DATA 7.57E+08 NO DATA 7.13E+08 ZN 59 0.00E+00 0,00E+00 0.00E+00 NO DATA 0.00E+00 NO DATA 0.00E+00 BR-83 NO DATA NO~ DATA NO DATA NO DATA NO DATA NO DATA NO DATA BR 84 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA BR 85 NO' DATA -N3 DATA NO DATA NO DATA NO DATA NO DATA NO DATA RB-86 NO DATA 4.87E+08 2.27E+08 NO DATA NO DATA NO DATA 9.61E+07 RB 8, NO DATA 0.00E+00 0.00E+00 NO DATA NO DATA NO DATA 0.00E+00 RB-89 NO DATA 0.00E+00' O.00E+00 NO DATA NO DATA NO DATA 0.00E+00 SR-89 3.01E+08 NO DATA 8.64E+06 NO DATA NO DATA NO DATA 4.83E+07 SR 90 1.24E+10 NO DATA 3.05E+09 NO DATA NO DATA NO DATA 3.59E+08 l SR-91 1.43E-10 NO DATA 5.79E l NO DATA NO DATA NO DATA 6.83E-10 SR-92 1.28E-49 hG DATA 5.54E-51 NO DA.A NO DATA NO DATA 2.54E-48
-Y-90 1 09E+02 NO DATA 2.92E+00 NO DATA NO DATA NO DATA 1.15E+06 CLINTON-1 3-119 Rev.5-2/89
. . - . .- _ . . . .. ~ . . . . .___
vu van TA]lLE 3.5-27 (continued)
MEAT PATHWAY FACTORS -R (ADULT)
(m2 mem/yr per #Ci/sec)
QPR AQE LIVER T. BODY THYROID KIDNEY MG GI-LLI ISOTOPE
. .Y-91m 0.00E+00 NO DATA 0.00E+00 NO DATA NO DATA NO DATA 0.00E+00 Y-91 1.13E+06 NO DATA 3.03E+04 NO DATA NO DATA NO DATA 6.23E+08 Y-92 1.49E 39 NO DATA 4.36E-41 NO. DATA NO DATA NO DATA 2.61E 35 Y-93 4.40E 12 NO DATA 1.21E-13 NO DATA NO DATA NO DATA 1.39E 07 ZR-95 1.87E+06 6.00E+05 4.06E+05 NO DATA 9.41E+05 NO DATA 1,90E+09 ZR 97 2,03E-05 4.10E-06 .1.88E 06 30 DATA 6.17E-06 NO DATA 1.27E+00 NB 95 2.30E+06 1.28E+06 6.86E+05 NO D*TA 1.26E+06 NO DATA 7.75E+09 MO 99 NO DATA 9.91E+04 1. 8? E+% Z .sTA 2.24E+05 NO DATA 2.30E+05 TC 99m 4.32E 21 1.22E 20 1.56E 19 NO DATA 1.86E 19 5.99E-21 7.23E 18 TC-101 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 0.00E+00 0.00E+00 RU-103 1.05E+08 NO DATA 4.53E+07 NO DATA 4.02E+08 NO DATA 1.23E+10 j RU-105 5.42E-28 NO DATA 2.14E-28 NO DATA 7.00E 27 NO DATA 3.32E-25 RU-106 2.81E+09 NO DATA 3.55E+08 NO DATA 5 . 47 5'+09 NO DATA 1.82E+11 AG-110m 6.67E+06 6.17E+06 3.67E+06 NO DATA 1.L NO DATA 2.52E+09 TE-125m 3.59E+08 1.30E+08 4.81E+07 1.08E+08 1. 46 t.+u 9 NO DATA 1.43E+09 TE-127m 1.12E+09 3.99E+08 1.36E+08 2.85E+08 4.54E+09- NO DATA 3.75E+09 TE 127. 2.09E-10 7,52E-11 4.53E-11 1.55E-10 8.53E-10 NO DATA 1.65E-08 TE-129m 1.13E+09 4.22E+08 1.79E+08 3.89E+08 4.73E+09 NO DATA -5.70E+09 TE 129 0.00E+ 00 0.00E+00 0.00E+00 0.00E+00 0 00E+00 NO DATA 0.00E+00
-TE-131m 4.50E+02 2.20E+02 1.83E+02 3.48E+02 2.23E+03 NO DATA 2.18E+04
- -TE-131 -0.00E+00 0.00E+00- 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 TE-132, 1.42E+06 9.21E+05 8.64E+05 1.02E+06 8.87E+06 NO DATA 4.36E+07 I-130 .2.03E-06 5.98E 06 2.36E-06 5.07E 04 9.33E 06 NO DATA 5.15E-06 I 131 1.07E+07 1.54E+07 8.80E+06 5.03E+09 2.63E+07 NO DATA 4.05E+06
'I-132- 7.13E-59 1.91E-58 6.67E-59 6.67E-57 3.04E-58 NO DATA 3.58E-59 I-133 3.70E-01 6.43E-01 1.96E-01 9.45E+01 1.12E+00 NO DATA 5.78E-01 I-134 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 I
'CLINTON-1 3-120 Rev.5-2/89
,G t'b - ODCM )
i i
TABLE 3.5-27 (continued)
MEAT PATHWAY FACTORS - R (ADULT)
(m2 mrem /yr per gci/sec)
^
. ORGAN! LIVER T. BODY THYROID KIDNEY J1EG GI LLI RQEE ISOTOPE I 135 4.65E 17 1.22E-16 4.49E-17 8.03E-15 1.95E-16 NO DATA 1.38E-16 CS-134 6.53E+08 1.55E+09 1.27E+09 NO DATA 5.03E+08 1.67E+08 2.72E+07 CS-136 1.20E+07 4.75E+07 3.42E+07 NO DATA 2.65E+07 3.63E+06 5.40E+06 CS-137 8.69E+08 1.19E+09 7.78E+08 NO DATA 4.03E+08 1.34E+08 2.30E+07
.CS 138 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 0.00E+00 0.00E+00
.DA-139 0.00E+00- 0.00E+00 0.00E+00 NO DATA 0.00E+00 0.00E+00 0.00E+00 BA-140 2.88E+0F 3.62E+04 1.89E+06 NO DATA 1.23E+04 2.07E+04 5.94E+07 BA-141 0.0CE+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 0.00E+00 0.00E+00 BA-142 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 0.00E+00 0.00E+00 IA-140 3.68E 02 1.85E-02 4.90E-13 NO DATA NO DATA NO DATA 1.36E+03
-LA-142 4.07E 92 1.85E 92 4.61E-93 NO DATA NO DATA NO DATA 1.35E-88 CE 141 1.39E+04 9.43E+03 1.07E+03 NO DATA 4.38E+03 NO DATA 3.61E+07 y CE-143 2.03E-02 1.50E+01 1.66E-03 NO DATA 6.61E 03 NO DATA 5.61E+02 CE-144 1.46E+06 6.10E+05 7.83E+04 NO DATA 3.62E+05 NO DATA 4.93E+08 PR-143 2.09E+04 -8.40E+03 1.04E+03 NO DATA 4.85E+03 NO DATA 9.17E+07 PR-144 0.00E+00 0.Ceb 00 0.00E+00 NO DATA 0.00E+00 .NO DATA 0.00E+00 ND-147 7.04E+03 3.1.. 03- 4.87E+02 NO DATA 4.76E+03 NO DATA 3.91E+07
% 187 2.06E 02 1.72E 02 6.02E 03 NO DATA NO DATA NO DATA 5.64E+00 NP-239. 2.?;c-01 2.53E-02 1.39E-02 NO DATA 7.88E-02 NO DATA 5.18E+03
- mrem /yr per 4Ci/m 3
- -1.45 x 10-3 l-CLINTON.1 3 121 Rev.5-2/89
s yrs-vuva TABLE 3.5-28 VEGETATION PA3WAY FACTORS - RY (CHILD)
(m2 mcm/yr per pci/sec)
ORGAN! 390f!E LIYJE T. BODY. THYROID KIDNEY MR[Q GI-LLI ISOTOPE _
H3 NO DATA 4.01E+03* 4.01E+03* 4.01E+03* 4.01E+03* 4.01E+03* 4.01E+03*
C-14 3.51E+06* 7.01E+05* 7.01E+05* 7.01E+05* 7.01E+05* 7.01E+05* 7.01E+05*
NA-24 3.75E+05** 3.75E+05 3.75E+05 3.75E+05 3.75E+05 3.75E+05 3.75E+05 P-32 3.37E+09 1.57E+08 1.30E+08 NO DATA NO DATA NO DATA 9.30E+07 ,
CR-51 NO DATA NO DATA 1.17E+05 o.49E+04 1.77E+04 1.18E+05 6.20E+06 MN-54 'NO DATA 6.64E+08 1.77E+08 NO DATA 1.86E+08 NO DATA 5.58E+08 MN-56 NO DATA 1.87E+01 4.22E+00 NO DATA 2.26E+01 NO DATA 2.71E+03 FE-55 8.02E+08 4.25E+08 1.32E+08 NO DATA NO DATA 2.40E+08 7.88E+07 FE 3.98E+08 6.43E+08 3.21E+08 NO DATA NO DATA 1.87E+08 6.70E+0S CO-58 NO DATA 6.44E+07 1,97.E+08 NO DATA NO DATA NO DATA 3.76E+08 CO 60 NO DATA 3.79E+08 1.12E+09 NO DATA NO DATA NO DATA 2.10E+09 NI-63 3.95E+10 2.11E+09 1.34E+09 NO DATA NO DATA NO DATA 1.42E+08
)
NI-65 1.05E+02 9.89E+00 5.77E+00 NO DATA NO DATA NO DATA 1.21E+03 CU-64 NO DATA 1.09E+04 6.59E+03. NO DATA 2.64E+04 NO DATA 5.12E+05 ZN-65 8.11E+08 2.16E+09 1.34E+09 NO DATA 1.36E+09 NO DATA 3.79E+08
-ZN-69 9.29E-06 1.34E 05 1.24E-06 NO DATA 8.14E-06 NO DATA 8.46E 04 BR 83 NO DATA NO DATA 5.40E+00 NO DATA NO DATA NO DATA NO DATA BR 84 NO DATA N0' DATA 3.92E-11 -NO DATA NO DATA NO DATA NO DATA BR 85 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA RB-86 NO DATA 4.53E+08 2.79E+08 NO DATA NO DATA NO DATA- 2.91E+07 RB 88 NO DATA' 4,38E-22 3.04E-22 NO DATA NO DATA NO DATA 2.15E 23 RB-89 NO DATA 4.69E-26 4.17E-26 NO DATA NO DATA NO DATA .4.09E-28
-SR-89 3.59E+10 NO DATA 1.03E+09 NO DATA NO DATA NO DATA 1.39E+09 SR 1.24E+12 NO DATA 3.14E+11 NO DATA NO DATA NO DATA 1.67E+10 SR-91 5.21E+05 NO DATA 1.97E+04 NO DATA NO DATA NO DATA 1.15E+06 SR-92' 7.29E+02 NO DATA 2.92E+01 NO DATA NO DATA NO DATA 1.38E+04 Y-90 2.31E+04 NO DATA 6,18E+02 NO DATA NO DATA NO DATA 6.58E+07 CLINTON-1. 3 122 Rev.5-2/89 l
l
\
vra vuun TABLE 3.5-28 (continued)
V VEGETATION PATHWAY FACTORS - R (CHILD)
(m2 mrem /yr per #Ci/sec)
-T. BODY THYROID KIDNEY Igiq GI LLI ORGAN: 3.QFJ LIV.EB ISOTOPE Y-91m 9.248-09 NO DATA 3.36E 10 NO DATA NO DATA NO DATA 1.81E-05 1.86E+07 NO DATA 4.97E+05 NO DATA NO DATA NO DATA 2.48E+09
=Y-91 Y-92 1.58E+00 NO DATA 4.52E-02 NO DATA NO DATA NO DATA 4.57E+04 2.92E+02 NO DATA 8.01E+00 NO DATA NO DATA NO DATA 4.35E+06 Y-93 ZR 95 3.86E+06 8.49E+05 7.56E+05 NO DATA 1.22E+06 NO DATA 8.86E+08 -
ZR-97 5.66E+02 8.18E+01 4.83E+01 NO DATA 1.17E+02 NO DATA 1.24E+07 NB-95 4.10E+05 1.60E+05 1.14E+05 NO DATA 1.50E+05 NO DATA 2.95E+08 MD-99 NO DATA 7.67E+06 1.90E+06 NO DATA 1.64E+07 NO DATA 6.35E+06 TC-99m 4.70E+00 9.21E+00 1.53E+02 NO DATA 1.34E+02 4.68E+00 5.24E+03 TC 101 1.48E-30 1.54E-30 1.96E-29 NO DATA 2.63E-29 8.16E 31 4.91E 30 RU-103 1.54E+07 NO DATA 5.90E+06 NO DATA 3.86E+07 NO DATA 3.97E+08 RU-105 9.16E+01 NO DATA 3.32E+01 NO DATA 8.05E+02 NO DATA 5.98E+04 RU-106 7.45E+08 NO DATA 9,30E+07 NO DATA 1.01E+09 NO DATA 1.16E+10 AG-110m 3.21E+07 2.17E+07 1.73E+07 NO DATA 4.04E+07 NO DATA 2.58E+09 TE-125m 3.51E+08 9.52E+07 4.68E+07 9.86E+07 NO DATA NO DATA 3.39E+08
.TE-127m 1.32E+09 3.56E+08 1.57E+08 3.16E+08 3.77E+09 NO DATA 1.07E+09 3.84E+05 TE-127 9.84E+03 2.65E+03 2.llE+03 6.81E+03 2.80E+04 NO DATA TE-129m 8.43E+08 2.35E+08. 1.31E+08 2.72E+08 2.47E+09 NO DATA 1.03E+09 TE-129 1.32E-03 3.68E 04 3.13E-04 9.42E-04 3.86E-03 NO DATA 8.21E-02 TE-131m 1.54E+06~ 5.33E+05 5.67E+05 1.10E+06 5.16E+06 NO DATA 2.16E+07 TE-131 2.59E 7.89E-16 7.71E-16 1.98E 15 7.83E-15 NO DATA 1.36E-14 TE-132 7.00E+06 3.10E+06 3.74E+06 4.51E+06 2.88E+07 NO DATA 3.12E+07 I-130 6.10E+05 1.23E+06 6.35E+05 1.36E+08 1.84E+06 NO DATA 5.77E+05 1-131 1.43E+08 1.44E+08 8.16E+07 4.75E+10 2.36E+08 NO DATA 1.28E+07 s -
I-132 9.20E+01 1.69E+02 7.77E+01 7.84E+03 2.59E+02 NO DATA- 1.99E+02 1-133 3.53E+06 4.36E+06 1.65E+06 8.llE+08 7.27E+06 NO DATA 1.76E+06 I 134 1.50E 04 2.79E 1.28E-04 6.41E-03 4.26E-04 NO DATA 1.85E-04 CLINTON-1 3-123 Rev.5-2/89
'uh.uybg TABLE 3.5-21 (continued)
VEGETATION PATHWAY FACTORS - RV aij(CHILD)
(m2 mrem /yr per pci/sec)
ORGAN: AQHE LIVER T. BODY THYROID KIDNEY LlPJ!G GI-LLI ISOTOPE I-135 6.28E+04 1,13E+05_ 5.34E+04 1.00E+07 1.73E+05 NO DATA 8.61E+04 CS-134 1.60E+10 2.63E+10 5.55E+09 NO DATA 8.15E+09 2.92E+09 1.42E+08 CS 136 8.23E+07 2.26E+08 1.46E+08 NO DATA 1.20E+08 1.80E+07 7.95E+06 CS-137 2.39E+10 2.29E+10- 3.38E+09 NO DATA 7.46E+09 2.68E+09 1.43E+08 CS-138; 6.44E 11 8.95E-11 5.68E-11 NO DATA 6.30E-11 6.78E 12 4.12E 11 BA-139' 4.97E 02 2.65E-05 44E-03 NO DATA 2.32E-05 1.56E-05 2.87E+00 BA-140 2,77E+08 2.42E+05 1.62E+07 NO DATA 7.89E+04 1.45E+05 1.40E+08 BA 141 2.04E-21 1.14E-24 6.64E-23 NO DATA 9.88E-25 6,71E-24 1.16E-21 BA 142 9.70E-39 6.98E 42 5.42E-40 NO DATA 5.65E 42 4.11E-42 1.27E-40 IA-140 3.24E+03 1.13E+03 3.53E+02 NG DATA .NO DATA NO DATA 3.16E+07 LA 142 3.39E-04 1.08E 04 3.38E 05 NO DATA NO DATA NO DATA 2.14E+01 CE-141 6.56E+05 3.27E+05 4.85E+04 NO DATA 1.43E+05 NO DATA 4.08E+08
)
CE-143 1.71E+03 9.29E+05 1.35E+02 NO DATA 3.90E+02 NO DATA 1.36E+07 CE-144 1.27E+08 3.99E+07 6.79E+06 NO DATA 2.21E+07 NO DATA 1.04E+10 PR.143 '1.45E+05 -4.37E+04 7.22E+03 NO DATA 2.36E+04 NO DATA 1.57E+08 PR 144 5.64E-26 1.74E 26 2.84E-27 '20 DATA 9.22E-27 NO DATA 3 .- 7 5 E- 2 3
-ND-147 7.16E+04 5.80E+04 4.49E+03- NO DATA 3.18E+04 NO DATA 9.18E+07 W-187 6.44E+04 3.81E+04 1.71E+04 NO DATA NO DATA NO DATA 5.36E+06 NP-239 2.56E+03- 1.84E+02 1.29E+02 NO DATA 5.31E+02 NO DATA 1.36E+07
- mrem /yr per pCi/m3
- 3.75x105 CLINTON-1 3 124 Rev.6 12/89
w vum TABLE 3.5-29 j VEGETATION PATHWAY FACTORS - R (TEEN)
(m2 mrem /yr per pCi/sec)
ORGAN: LIVER T. BODY THYROID FIDNEY L12dG 01 LLI 1911E ISOTOPE H3 NO DATA 2.59E+03* 2.59E+03* 2.59E+03* 2.59E+03* 2.59E+03* 2.59E+03*
c.14 1.45E+06* 2.91E+05* 2.91E+05* 2.91E+05* 2.91E+05* 2.91E+05* 2.91E+05*
NA 24 2.40E+0$** 2.40E+05 2.40E+05 2.40E+05 2.40E+05 2.40E+05 2.40E+05 j l
P 32 1.61E+09 9.97E+07 6.24E+07 NO DATA NO DATA NO DATA 1.35E+08 CR-51 NO DATA NO DATA 6.12E+04 3.40E+04 1.34E+04 8.74E+04 1.03E+07 MN 54 NO DATA 4.54E+08 9.01E+07 NO DATA 1.36E+08 NO DATA 9.32E+08 l
MN 56 NO DATA 1.43E+01 2.54E+00 NO DATA 1.81E+01 NO DATA 9.41E+02 FE 55 3.26E+08 2.31E+08 5.39E+07 NO DATA NO DATA 1.46E+08 1. 00 E+.08 i FE 59- -1.79E+08 4.18E+08 1.61E+08 NO DATA NO DATA 1.32E+08 9.88E+08 l CO-58 NO DATA 4.36E+07 1.01E+08 NO DATA NO DATA NO t.ATA 6.02E+08 Co 60 NO DATA 2.49E+08 5.60E+09 NO DATA NO DATA NO DATA 3.24E+09 i NI 63 1.61E+10 1.14E+09 5.46E+08 NO DATA NO DATA NO DATA 1.81E+08 NI 65 5.73E+01 7.32E+00 3.34E+00 NO DATA NO DATA NO DATA 3.97E+02 CU 64 NO DATA 8.28E+03 3.90E+03 NO DATA 2.10E+04 NO DATA 6.42E+05 ZN-65 4.23E+08 1.47E+09 6.86E+08 NO DATA 9.41E+08 NO DATA 6.23E+08 ZN 69= 5.04E-06 9.60E 06 6.72E 07 do DATA 6.28E 06 NO DATA 1.77E 05 BR-83 NO DATA NO DATA- 2.93E+00 NO DATA NO DATA NO DATA NO DATA BR 84 NO DATA NO DATA 2.31E 11 NO DATA NO DATA NO DATA NO DATA BR 85 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA
. RB 86 NO DATA 2.72E+08 1.28E+08' NO DATA NO DATA NO DATA 4.02E+07 RD 88 NO DATA 3.17E 22 1.69E 22 NO DATA NO DATA NO DATA 2.72E 29
- RB 89 NO DATA 3.56E 26 2.52E 26 NO DATA NO DATA NO DATA 5.45E 35 SR-N9 1.51E+10 NO DATA 4.32E+08 NO DATA NO DATA NO DATA 1.80E+09 SR 90 7.50E+11 NO DATA- 1.85E+11- NO DATA NO DATA NO DATA 2 .11i.+10 i
NO DAT/ 1.12E+04 NO DATA NO DATA 1. 2 8 E+,.6 j' SR-91 2.82E+05 NO DATA.
NO DATA 1. 70 E+01 NO-DATA NO DATA NO DATA 1,02E+04 SR 92 . 4.00E+02 Y 90 1.25E+04 NO DAT* 3.37E+02 NO DATA NO DATA NO DATA 1.03E+08 L
l L
i
! -CLINTON 1 3 125 Rev.5-2/89
-,,p. .r,e-, ,. ,.,,-,,,,-c.,,,-,.n -. - -me. e . - , - , ,.,w, , ,, ,._4. _ _ . _ _ _ ,,___w,,,,,.___-__,____,___,~_-,.,s-, -
. . n, e-.._.-
CPS 0DCM i
TABLE 3.5-29 (continued) j VEGF.TATION PATHWAY FACTORS - R (TEEN)
(m2 mrem /yr per sci / soc) i ORCAN: f^E LIVER T. BODY THYROID YIDNEY Lla(Q CI LLI ISOTOPE ,
Y 91m 5.04E 09 NO DATA 1.93E 10 NO DATA No DATA NO DATA 2.38E 07 Y 91 7.84E+06 NO DATA- 2.10E+05 NO DATA NO DATA NO DATA 3.21E+09
- x Y 92 8.60E 01 NO DATA 2.49E 02 NO DATA NG DATA NO DATA 2.36E+04 I
Y 93 1.58E+02 NO DATA 4.34E+00 NO DATA NO DATA NO DATA 4.83E+06 I ZR 95 1.73E+06 5.46E+05 3.75E+05 NO DATA 8.02E+05 NO DATA 1.26E+09 ;
ZR-97 3.10E+02 6.14E+01 2.83E+01 NO DATA 9.31E+01 NO DATA 1,66E+07 NB-95 1.92E+05 1.07E+05 5.86E+04 NO DATA 1.03E+05 NO DATA 4.56E+08
- MO 99 NO DATA 5.64E+06 1.08E+06 NO DATA 1.29E+07 NO DATA 1.01E+07 TC 99m - 2.73E+00 7.61E+00 9.86E+01 NO DATA 1.13E+02 4.23E+00 5.00E+03 TC 101: 8.02E 31 1.14E 30 1.12E 29 NO DATA 2.06E 29 6.95E 31 1.95E 37 RU 10:1- 6.81E+06 NO-DATA 2.91E+06 NO DATA 2.40E+07 NO DATA 5.69E+08 RU 105 4.97E+01 NO DATA 1.93E+01 NO DATA 6.27E+02 NO DATA 4.01E+04 ,
J.
RU 106 3.09E+08 NO DATA 3.89E+07 NO DATA 5.95E+08 NO DATA 1.48E+10 A0 110m 1.51E+07 1.43E+07. f.72E+06 NO DATA 2.73E+07 No DATA 4.03E+09 TE 125m 1.49E+08. 5.35E+07 1.99E+07 4.15E+07 NO DATA NO DATA 4.38E+03 TE 127m : 5.52E+08 1.96E+00 6.57E+07 1.31E+08 2.24E+09 NO DATA 1.38E+09 TE 127 5.40E+03 1.92E+03 1.16E+03 3.73E+03 2.19E+04 NO DATA 4.17E+05 TE 129m _ 3.60E+08 1.34E+08 5.70E+07 1.16E+08 1.51E+09 NO DATA 1.35E+09 TE 129 7.13E 04 2.66E 04 1.73E 04 5.09E 04- 2.99E 03 NO DATA 3.90E 03 TE 131m 8.44E+05. 4. 05E+05 3.38E+05 6.09E+05 4. 22E4 06 NO DATA 3.25E+07 TE 131 1.41E 15 5.80E-16 4.39E 16 1.08E 15 6.15E 15 NO DATA 1.15E 16
- TE 132 . 3.91E+06 2.48E+06 2.33E+06 2.61E+06 2.37E+07 NO DATA 7.84E+07
- 14130 . 3.50E+05 1.01E+06 4.05E+05 8.26E+07 1.56E+06 NO DATA 7.79E+05
- I 131 7.66E+07 1.07E+08 5.76E+07 S.13E+10 1.85E+08 NO DATA 2,12E+07 I 132 5.19E+01 1.36E+02 14.87E+01 4.58E+03 2.14E+02 NO DATA 5.91E+01 1 133- 1.93E+06' 3.28E+06 1.00E+06 4.58E+08 5.75E+06 NO DATA 2.48E+06 I 134 8,44E 05- 2.24E 04 8.03E 05 3.73E 03 3,53E 04 .NO DATA 2.95E-06
- CLINTON 1~ 3 126 Rev.5 2/89 4
- e. a 4_.. -r.,,.. - . . +,~,,.-r._ -,._.m,,r, ,m.,_.-.-.m._ ,.-_,ve.,.,..-_m-. ._,,~n .y..,. , . , . ,...,-.,rr 1
--*ir =w--v---, -,w-. --h-+--t-
CPS 0DCM TABLE 3.5-29 (cositinued)
VEGETATION PATINAi FACTORS - R (TEEll) .
(m2 nrom/yr por pCi/ soc)
QuGN11, E LIVET T 30DY Tir!ROiD KIDNFY M CI LLI ISOTOPE 9.09E+04 3.37E+04 5.85E+06 1.44E+05 NO DATA 1.01E+05 2 135 3.53E+04 1.67E+10 7.75E+09 1:0 DATA 5.31E+09 2.03E+09 2.08E+08 CS 134 7.10E+09 1.72E+08 1.16E+08 NO DATA 9.37E+07 1.48E+07 1.38E+07 CS 136 4.37E+07 1.35E+10 4.70E+09 NO DATA 4.59E+09 1.78E+0" 1.92E+08 CS 137 1.01E+10 3,08E 14
-CS 138 'J.54E 11 6.80E 11 3.40E 11 NO DATA 5.02E 11 5.84E 2.70E 02 1.90E 05 7.86E 04 NO DATA 1.79E 05 1.31E.. . 2.41E 01
-3A 139 1.69E+05 8.89E+06 NO DATA 5.73E+04 1.14E+05 1.13E+08 BA 140 1.38E+08 1.11E 21 8.27E-25 3.70E 23 NO DATA 7.67E 25 5.66E 25 2..:5E 27 BA 141 5.35E 42 3.29E 40 NO DATA 4.53E 42 3.56E 42 1.64E 50 BA 142 5.35E-39 8.86E+02 2.36Et02 NO DATA NO DATA NO DATA 5.09E+07 LA-140 1.80E+03 8.35E 05 2.08E 05 NO DATA NO DATA NO DATA 2.54E+00 1A-142 1.88E 04
-1.89E+05 2.17E+04 NO DA1A 8.90E+04 No DATA 5.41E+08 CEd41 2.83E+05 l
7.58E+01 NO DATA 3.04E+02 NO DATA 2.04E+07 CE 143 9.33E+02 6.79E+05 2.19E+07 2.84E+06 NO DATA 1.31E+07 NO DATA 1.33E+10 CE 144 5.29E+07 3.48E+03 NO DATA 1.62E+04 NO DATA 2.30E+08 PR 143 7.00E+04 2.79E+04 1.24E 26 1.54E 27 NO DATA 7.14E 27 NO DATA 3.35E 29 PR 144 3.04E 26'
-3.62E+04 3.94E+04 2.36E+03 NO DATA 2.31E+04 NO DATA 1.42Et08 ND 147 7.79E+06-2.88E+04' l'. 01E+04 NO. DATA NO DATA NO *.)ATA W 187. 3.53E+04 1.31E+02 7.26E+01 NO DATA 4.10E+02 NO DATA 2.10E+07 N?.239 1.39E+03
- mrem /yr por 4Ci/m 3
- 2.40x10 5 3-127 Rev.5-2/89 CLINTON 1
l TABLE 3.5-30 VEGETATION PATHWAY FACTORS - R ( ADUIll)
(m2 mrom/yr per uci/sec)
ORGAN: SQL{E LIVER Il@Y THYROID YIDNEY LL'llg GI LLI ISOTOPE H3 NO DATA 2. 26 E+ 03
- 2.26E+03* 2.26E+03* 2.26E+03* 2.26E+03* 2.26E+03*
C 14 8.97E+05* 1.79E+05* 1.79E+05* 1.79E+0$* 1.79E+05* 1.79E+05* 1.79E+05*
NA 24 2.71E+0$** 2.71E+05 2.71E+05 2.71E+05 2.71E+05 2.71E+05 2.71E+05 P 32 1.40E+09 8.70E+07 5.41E+07 NO DATA NO DATA NO DATA 1.57E+0S CR 51 NO DATA NO DATA 4.60E+04 2.75E+04 1.01E+04 6.11E+04 1.16E+07 MN 54 NO DATA 3.13E+08 5.960+07 NO DATA 9.30E+07 NO DATA 9.38E+08 MN 56 NO DATA 1.59E+01 2.82E+00 NO DATA 2 01E+01 NO DATA 5.06E+02 FE 55 2.10E+08 1.45E+08 3.38E+07 NO DATA NO DATA 8.10E+07 8.33E+07 FE 59 1.26E+08 2.96E+08 1.13E+08 NO DATA NO DATA 8.27E+07 9.86E+08 Co 58 NO DATA 3.08E+07 6.90E+07 NO DATA NO DATA NO DATA 6.24E+08 CO 60 NO DATA 1.67E+08 3.69E+08 NO DATA NO DATA NO DATA 3.14E+09 NI 63 1.04E+10 7.21E+08 3.49E+08 NO DATA NO DATA NO DATA 1.50E+08
)
NI 65 6.18E+01 8.03E+00 3.66E+00 NO DATA NO DATA NO DATA 2.04E+02 CU 64 NO DATA 9.16E+03 4,30E+03 NO DATA 2.31E+04 NO DATA 7.81E+05 ZN-65 3.18E+08 1.01E+09 4.57E+08 NO DATA 6.76E+08 NO DATA 6.36E+08 ZN 69 5.39E 06 1.03E 05 7.17E 07 NO DATA 6.69E 06 NO DATA 1.55E 06 BR 83 NO :PTA NO DATA 3.13E+00 NO DATA NO DATA NO DATA 4.50E+00 BR 84 NO DATA NO' DATA 2.54E-11 NO DATA NO DATA NO DATA 1.99E 16 BR 85 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA RB 86 NO DATA 2.19E+08 1.02E+08 NO DATA NO DATA NO DATA 4.33E+07 RB 98 NO DATA 3.43E 22 1.82E 22 NO DATA NO DATA M0 DATA 4.74E-33 RB 89 NO DATA 3.96E 26 2.79E 26 NO DATA No DA' NO DATA 2.30E-39 SR 89 9.95E+09 NO DATA 2.86E+08 NO DATA NO DATA NO DATA 1.60E+09 SR 90 6.04E+11 NO DATA 1.4BE+11 NO DATA NO DATA NO DATA 1.75E+10 SR-91 3.02E+05 NO DATA 1.22E+04 NO DATA NO DATA NO DATA 1. 44 E+ 06 SR 92 4 28E+02 NO DATA 1.85E+01 NO DATA NO DATA NO DATA 8.48E+03 Y-90 1.33E+04 NO DATA 3.56E+02 NO DATA NO DATA NO DATA 1.41E+08 CLINTON 1 3 128 Rev.5 2/89
1 CTS.0DCM TABLE 3.5-30 (continued)
Y VEGETATIO!! PATHWAY FACTORS - R (ADULT)
(m2 mrom/yr por sci /sec)
T. BODY THYROID YIDNEY ]1TG GI-LLI '
ORGAN: AQUE LIVER ISOTOPE l Y 91m 5.42E.09 NO DATA 2.10E.10 NO DATA NO DATA NO DATA 1.59E.08 l Y.91, NO DATA 1.37E+05 NO DATA NO DATA NO DATA 2.82E+09 i 5.12E+06 2.67E.02 NO DATA NO DATA NO DATA 1.60E+04 Y.92 9.13E 01 No DATA i 1.69E+02 NO DATA 4.65E+00 NO DATA NO DATA NO DATA 5.35E+06 Y 93 3.79E+05 2.56E+05 NO DATA 5.94E+05 NO DATA 1.20E+09 ZR.95 1.18E+06 ,
6.78E+01 3.10E+01 NO DATA. 1.02E+02 NO DATA 2.10 E+07 i ZR.97 3.36E+02
- 7. 91E404 4.25E+04 NO DATA 7.82E+04 NO DATA 4.80E+08- ;
NB.95 1.42E+05 6.12E+06 1.16E+06 No DATA 1.39E+07 NO DATA 1.42E+07 -
H0 99 NO DATA 5.16E+03 TC 90m 3.09E+00 8.73E+00 1.11E+02 NO DATA 1.33E+02 4.28E+00 i
1.24E-30 1.22E.29 NO DATA 2.24E 29 6.35E.31 3.73E.42' -
TC 101 8.6?b 21 NO DATA 5.57E408 I
RU.103 4.77E+06 NO DATA 2.06E+06 NO DATA 1.82E+07 NO DATA 2.12E+01 NO DATA 6.93E+02 NO DATA 3.28E+04 _,
RU.105 5.36E+01 i
NO DATA 2.44E+07 NO DATA 3.73E+08 NO DATA 1.25E+10 RU 106 1.93E+08 3.98E409 9.75E+06 5.79E+06 No DATA 1.92E+07 NO DATA AC 110m 1.05E+07 4
1.30E+07 2.91E+07 3.93E+08 NO DATA 3.86E+08 TE.125m 9.67E+07 3.51E+07 ,
4.26E+07 8,93E+07 1.42E+09- NO DATA 1.17E+09 TE.127m 3.49E+08 1.25E+0C 1.22E+03 4.19E+03 2.30E+04 NO DATA 4.46E+02 TE.127 5.65E+03 2.03E+03 3.97E+07 8.61E+07 1.05E+09 NO DATA 1.26E+09 TE.129m 2.51E+08 9.35E+07 2.86E 04 1.85E 04 5.84E 04 3.20E.03 NO DATA 5.75E.04 TE 129' 7.61E 04 4.43E+07 TE.131m 9.12E+05 4.46E+05 3.72E+05 7.06E+05 4.52E+06 NO DATA 6.32E.16 4.78E.16 1.24E.15 6.63E.15 NO DATA 2.14E.16 TE 131- 1.51E-15 L
2.62E+06 3.08E+06 7.68E+07 NO DATA 1.32E+0B TEL132 4.31E+06 2.79E+06 4.55E+05 9.77E+07 1.80E+06 NO DATA 9.93E+05 I.130 -3.91E+05 1.15E+06 3.05E+07 1.15E+08 6.62E+07 3.78E+10 1.98E+08 NO DATA 1 131' 8.07E+07 l'
5.40E+03 2.46E+02 NO DATA 2.90E+01 I 132' 5.77E+01 l'54E+02 5.40E+01 1.11E+06 5.34E+08 -6.34E+06 NO DATA 3.26E+06 I 133 2.09E+06 3.63E+06 9.06E.05 4.39E 03 4.03E.'04 NO DATA 2.21E 07 I 134 9.33E 05 2,53E 04
- CLINTON.1 3 129 Rev.5 2/89
+.,--a..-+..e,+.~. -mm.,..--,.-ye,,--,,em 3 o- . . - ...,o
, - , - ., ,w--.r-- .,p.-n-. -,---=-gr.prm,.,--wrpr~w-.r4 r. ,,.o,--v.,---
..we. m.....rm.
%vk.uut n ,
i TABLE 3.5-30 (continued)
VEGETATION PATHWAY FACTORS - R Y (ADULT)
(m2 mrem /yr por #C1/noc)
ORGAN: EQE LIEE T. BODY T*M101D KIDNEY LLPdg GI.LLI J1QTOPE I.135 3.91E+04 1.02E+05 3.77E+04 6.75E+06 1.64E+05 NO DATA 1.16E+05 C5 134 4.67E+09 1.11E+10 9.08E+09 NO DATA 3.59E+09 1.19E+09 1.94E+08 CS.136 4.26E+07 1.68E+08 1.21E+08 NO DATA 9.35E+07 1.28E+07 1.91E+07 l
l CS.137 6.36E+09 8.70E+09 5.70E+09 NO DATA 2.95E+09 9.82E+08 1.68E+08 CS.138 3.84E.11 7.58E.11 3.75E.11 NO DATA 5.57E.11 5.50E.12 3.23E.16 BA.139 2.86E 02 2.04E.05 8.38E.04 NO DATA 3.91t.05 1.16E.05 5.07E.02 BA.140 1.29E+08 1.62E+05 8.43E+06 NO DATA 5.50E+04 9.26E+04 2.65E+08
--. BA 141 1.18E.21 8.90E.25 3,98E.23 NO DATA 8.28E.25 5.05E.25 5.55E.31 BA.M2 $.79E.39 5.96E.42 3. 64 E.40 NO DATA 5.03E.42 3.37E.42 8.16E.57 L
1A.140 1.98E+03 9.95E+02 2.63E+02 NO DATA NO DATA NO DATA 7.31E+07 1A 142 2.04E.04 9.25E.05 2.31E.05 NO DATA NO DATA NO DATA 6.76E.01 CE.141 1.97E+05 1.33E+05 1.51E+04 NO DATA 6.19E+04 NO DATA 5.09E+08 i
CE.143 9.98E+02 7.38E+05 8.17E+01 NO DATA 3.25E+02 NO DATA 2.76E+07 CE.144 3.28E+07 1.37E+07 1.76E+06 N0' DATA 8.14E+06 NO DATA 1.11E+10 PR 143 6.26F+04. 2.51E+04 3.10E+03 NO DATA 1.45E+04 NO DATA 2.74E+08 PR 144 3.25E.26 1.35E.26 1.65E.27 NO DATA 7.61E.27 NO DAT,. 4.68E.33 ND.147 3.33E+04 - 3.85E+04 2.31E+03 NO DATA 2.25E+04 NO DATA . 1.85E+08 W.187 3.80E+04 3.18E+04 1.11E+04- NO DATA NO DATA NO DATA 1.40E+07 NP.239 1.43E+03 1.40E+02 7.74E+01- NO DATA 4.38E+02 NO DATA 2.88E+07 o'mrom/yr por #Ci/m 3 o* 2.71x10 5 i
-CLINTON.1 3 130 Rev.5 2/89
+
--.,,-r+ - ~ , - ,-,,--Yv.,,%-,-w-,- .m.,- s, -.y h=--9.~,,..,.. v -u.-..y, ,-h,..y .,y. , y 3.,a,.y gm , _e.-m,.mm--, %- r+--y.Sc-, ----m,-g
CPS 0DCM TABLE 3.5-31 G i GROUND PLANE PATHWAY FACTORS - R (m2 mren/yr per #Ci/sec)
Total Total Total Body Shin Isotooe Body Skin Jsotone . Body Skin Isotone H3 0. 00E4 00 0.00E+00 Y 91 1.07E+06 1.21E+06 CS-136 1.51E+08 1.71E+08 C 14 0.00E+00 0.00E+00 Y-92 1.80E+05 2.14E+05 CS 137 1.30E+10 1.52E+10 NA 24 1.20E+07* 1.39E+07 Y 93 1.83E+05 2.50E+05 CS-138 3.59E+05 4.10E405 P 32' O.00E+00 0.00E400 ZR 95 2.45E+08 2.85E+08 BA 139 1.06E+05 1.19E+05 CR 51 4.65E+06 5.50E+06 ER-97 2.96E+06 3.44E+06 BA 140 2.05E+07 2.35E+07 MN 54 1.38E+09 1.62E+09 NB 95 1.37E+08 1.61E+08 BA 141 4.17E+04 4.75E+04 KN 56 9.03E+05 1.07E+06 MO 99 3.99E+06 4.62E+06 BA-142 4.49E+04 5.11E+04 FE 55 0.00E+00 0.00E+00 TC-99m 1.84E+05 2.11E+05 LA 140 1.92E+07 2.18E+07 FE 59 2.73E+08 3.20E+08 TC 101 2.03E+04 2.26E+04 LA 142 7.60E+05 9.12E+05 RU 103 1.08E+08 1.26E+08 CE-141 1.37E+07 1.54E+07 CO 58 3.80E+08 4.45E+08 CO 60 , 2.32E+10 2.73E+10 RU-105 6.36E+05 7.21E+05 CE 143 2.31E+06 2.63E+06 NI 63 - 0.00E+00 0.00E+00 RU 106 4.22E+08 5.06E+08 CE 144 6.96E+07 8.05E+07
)
N1 65 2.97E+05 3.45E+05 AG 110m 3.44E+09 4.01E+09 PR-143 0.00E+00 0.00E+00 CU 64 6.05E+05 6.86E+05 TE 125m 1.56E+06 2.13E+06 PR 144 1. 84 E+ 03 2.11E+03 ZN-65 7.48E+08 8.60E+08 TE 127m 9.16E+04 1.08E+05 ND 147 8.39E+06 1.01E+07 ZN 69 - 0,00E+00 0.00E+00 TE 127 2.99E+03 3.29E+03 W 187 2.35E+06 2.73E+06 BR 83 4.87E+03 7.07E+03 TE-129m 1.98E+07 2.31E+07 NP 239 1.71E+06 1.98E+06 BR 84 2.03E+05 2.36E+05 TE-129 2.64E+04 3.12E+04 BR 85 0.00E+00 0.00E+00 TE 131m 8.02E+06 9.46E+06 RB-86 8.98E+06 1.03E+07~ TE-131 2.92E+04 -3.45E+04 RB 88 3.31E+04 3.78E+04 TE 132 4.24E+06 4.99F+06 RB 89 1.23E+05 1.48E+05 I 130 5.50E+06 6.68E+06
.SR 89 2.16E+04 2.50E+04 I 131 1.72E+07 2.09E+07 SR-90 NO DATA NO DATA I-132 1.25E+06 1.47E+06 SR 91' 2.14E+06 2.51E+06 I-133 2.45E+06 2.98E+06 SR 92 ,7.77E+05 8.64E+05 I-134 4.46E+05 5.30E+05 Y 90 4.50E+03 5.31E+03 1-135 2.53E+06 2.95E+06 Y 91m 1.00E+05 1.16E+05 CS-134 6.87E+09 8.01E+09 *1.20 x 10 7 CLINTON 1 3-131- Rev.5-2/89 i
-.,y v -y J,w w e +-r=--vv,-y, ,w-vrg- ww- g-v,-w,erw .w. w -.i mw vy-wyw-,-w-,.mw-- a w- r' -e i rwv y n-w - uw , -rustm---*.13-7s + -- *.m*-e-----nw---em-*- ==-n.wrwmme--
- ,ww-**w****=*rw--rarre=-=
CPS-ODCM 4.0 COMPLIANCE WITH 40CFR190 4.1 Total Dose - Operation and Surveillance Requirements OPERATION REOUIREMENT The annual (calendar year) dose or Jose 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 mrem to the total body or any organ, except the thyroid, which shall be limited to less than or equal to 75 mrom. This requirement is applicable at all times.
REMEDIAL REOUIREMEHIt
- a. With the calculated doses from the release of radioactive materials in liquid or gaseous effluents exceeding twice the limits of Sections 2.4.1(a), 2.4.1(b), 3.5.l(a), 3.5.1(b),
3.5.2(a), and 3.5.2(b), calculations shall be made including direct radiation contributions from the reactor unit and from outsido storage tanks to determine whether the above limits of Section 4.1 have been exceeded. If such is the case, preparc and submit to the Regional Administrator of the Regional Office of the NRC within 30 days 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 Part 20.405c, shall include the following information:
- 1. A determination of which uranium fuel cycle facilities or operations, in addition to CPS, contribute to the annual dose to the maximum exposed individual. Fuel cycle facilities located beyond the 5-mile radius from CPS need not be considered in this determination.
- 2. A determination of the maximum exposed individual.
- 3. A determination of the total annual dose to the maximum exposed individual from all existing pathways and sources of radioactivity and radiation (including direct radiation from N-16, the plant and storage facilities) using methodologies described in this manual. The direct radiation dose may be either calculated using NUREG-0133 methodolgy or measured.#
- The total body and organ doses resulting from liquid effluents will be summed with the doses resulting from gaseous effluents (including non-noble gases) and the doses to the maximum exposed individual from other operations of the uranium fuel cycle. The effluent doses will be based upon releases from CPS during the previous three quarters and from the quarter in which the Section 4.1 OPERATION REQUIREMENT was exceeded.
CLINTON-1 4-1 Rev.6-12/89
CPS-0DCM
- 4. It shall describe the 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 inc.3ude 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.
SURVEILIANCE REQUIREMENTS 4.1.1 Cumulative done contributions from liquid and gaseous affluents shall be determined in accordance with Sections 2.4.1.1, 3.5.1.1, and 3.5,2.1, and in accordance with the methodology and parameters described or specified in this me.nual.
4.1.2 Cumulative dose contributions from direct radiation from the reactor and from radwaste storage tanks shall be determined in accordance with the methodology and parameters described or specified in this manual. This requirement is applicable only under conditions set forth in the Remedial Requirement specified above (Section 4.1).
)
CLINTON-1 4-2 Rev.6-12/89 i
- - _ _ _ _ _ - _ . _ _ _ _ 1
. _ _ _ _ . _ . - . . _ _. .._. _ _ _ . . . . _ - _ ____ _ ._ ._.___.___.m.______ __.
CPS-ODCM 5.0 RADIOLOGICAL Elfv1RoliMEliTAL MOffITORI11G PROGRAM The primary requirements for the clinton Power Station Radiological Environmental Monitoring Program (REMP) are set forth in Section 5.1 of this manual.
supplomontal REMP ramplos required by commitmonts in the Environmental Report - Operating License Stage ( ER-OLS ) are described in Tablo 5.1-4 and Figures 5.0-1, 5.0-2, 5.0-3, and 5.0-4.
In addition to the required sampling program, CPS will perform supplemental periodic and long term sa:npling and analyses in order to better monitor the environmental exposure pathways. These samples will not be listed in this manual, however, full sample descriptions and results will be included in the Annual Radiological Environmental Operating Report.
Surface and drinking water samples are composited Ly collecting aliquots-of fixed volume at fixed time intervals. This method of sampling is considered consistent with note (g) in Table 5.1-1.
R,.:
CLINTON-1 5-1 Rev 6-12/89
,...-.m.-L.,.-,_,--, E r- r. _._,_y., ,_ ..w, ,_ m __
c m.'. m_ . , _ _ . - _ , . ,..,.r--.- r ~--r yve- ~ cw-.- -m+,-- -iv--- ----,y re,-->-w'-e-mym' ,ir- +t-
CPS-ODCM 5.1 Monitoring Program - Operation and Surveillance Requirements OPERATION RE00TREMENT The Radiological Environmental Monitoring Program shall be conducted as specified in Tet1.c 5.1-1. This requirement applies at all times.
REMEDIAL REOUIREMENT
- 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 Technical Specification 6.9.1.6, a de3cription of the reasons for not conducting the program as ,
required and the plans for preventirg a recurrence.
- b. With the level of radioactivity as the result of plant effluents in an environmental. sampling medium at a specified location exceeding the report levels of Table 5.1-2 when
, averaged over any calendar quarter prepare and submit to ths Regional Administrator of the Rogional Office of the NRC within 30 days a Special Report that identifies the cause(s) for exceeding the limit (s) and defines the corrective actions to be taken to reduce potential annual dese" to radioactive a MEMBEReffluents OF THE PUBLIC so that isthe less than the calendar year limits of Section 2.4.1, 3.5.1, and 3.5.2.
When more than one of the radionuclides in Table 5.1-2 are detected in the sampling medium, this report shall be I submitted if:
concentration (1) + concentration (2) + .. 21.0 reporting level (1) reporting level (2)
When radienuclides other than those in Tablethis 5.1-2report are shall detected and the result of plant effluents be submitted if the potential annual dose *,to a MEMBER OF THE PUBLIC is equal to or greater than the calendar year limits of Section 2.4.1, 3.5.1, and 3.5.2. This report is not required if the measured level of radioactivity was not the result of plant offluentsi however, in such an event, the condition shall be reported and described in the Annual . Rad.iological '
Environmental Operating Report.
- c. With milk or fresh leafy vegetation samples unavailable from one or more of the sample 1ccations required by Table 5.1-1, identify locations for obtaining replacement samples and add them to the radiological environmental monitoring program
- *The methodology and parameters used to nstimate the potential annual dose'to a MEMBER OF THE PUBLIC shall be indicated in this report.
i CLINTON-1 5-2 Rev.6-12/89 L,- . -_ ,_ _ ,_. _ , ,, _ _ _ _ __ ___ _ _ _
CPS-ODCM OPERATION RFOUTREMENT fMonitorina Procrari (continued 5.1 REMEDIAL REQUIREMENT (Continuedit within 30 days The specific locations from which samples were unavailabic may then be deleted from the monitoring program. Pursuant to Technical Specification 6.9.1.7, identify the cause of the Javailabi'.ity of samples and identify the nov location (s) for obtaining replacement samples in the next Semiannual Radioactive Effluent Release Report and also include in the report a revised figure (s) and table for this manual reflecting the new location (s).
StJRVEILLANCE REOUTREMENTS 5.1.1 The radiological environmental monitoring samples shall be collected pursuant to Table 5.1-1 from the specific locations given in Table 5.1-1 and Figures 5.0-1, 5.0-2, 5.0-3, and 5.0-4 and shall be analyzed pursuent to the requirements of Table 5.1-1 and the detection capabilities required by Table 5.1-3.
I CLINTON-1 5-3 Rev.6-12/89
I CPS-ODCM TABLE 5.1-1 RADIGIDGICAL ENVIRONMENTAL MONTTORING PROGRAM SAMPLING AND TYPE AND FREQUENCY I EXPOSURE PATHWAY NUMBER OF REPRESENTATIVE a OF ANALYSIS SAMPLES AND SAMPLE _JACATIONS C
_OLLECTION r'REOUENCY AND/OR SAMPLE.
b 40 routine monitcring stations Quarterly Gamma dose
- 1. DIRECT RADIATION quarterly.
either with two 9r more dosi-meters or with one instrument for measuring and recording dose rate continuously, placed l
as follows:
I (1) an inner ring of stations, I
one in each meteorological sector in the general area of.the SITE BOUNDARY; SECTOR CODE DTSTANCE from station (miles)
N CL-36 0.6 NNE CL-5 0.7 NE CL-22 0.6 ENE CL-23 0.5 E CL-24 0.5 ESE CL-42 - 2.8 SE CL-43 2.8 l
SSE CL-44 2.3 I
S CL-45 2.8 SSW CL-46 2.8 SW CL-47 3.3 WSW CL-48 2.3 W CL-1 1.8 WNW CL-34 0.8 NW CL-35 0.7 NNW CL-63 1.3 5 -- 4 Rev.6-12/89 CLINTO
CPS-ODCf TAllLE 5.1-1 (Continued)
RADIGILGICAL ENVIRONMENTAL MONITORING PROGRAM EXPOSURE PATHWAY NUMBER OF REPRESENTATIVE a SAMPLING AND TYPE AND FREQUENCY AND/OR SAMPLE SAMPLES AND SAMPLE LOCATIONS COLLECTION FREOUENCY OF ANALYSIS
- 1. DIRECT RADIATION b (2) an outer ring of stations, (Continued) one in each meteoroirsical sector in the 6 to 8.km (3.7 miles to 5.0 miles) range from the site; SECTOR CODE DISTANCE from station failes)
N CL-76 4.6 NNE CL-77 4.5 NE CL-78 4.8 -
ENE CL-79 4.5 E CL-53 4.3 ESE CL-54 4.6 SE CL-55 4.1 '
SSE CL-56 4.1 S CL-57 4.6 ,
t SSR CL-58 4.3 SW CL-60 4.5 WSW CL-61 4.5 W CL-80 4.1 WNW CL-81 4.5 NW CL-51 4.4 '
NNW CL-52 4.3 i
I l
t CLINTON-l' 5-5 Rev.6-12/89 i
CPS-ODCM-
~
TABLE 50 1-1-(Continued)
. RADIOIDGICAL ENVIRONMENTAL MONITORING PROGRAM EXPOSURE PATHWAY NUMBER OF REPRESENTATIVE a SAMPLING AND TYPE AND FREQUENCY AND/OR SAMPLE SAMPLES AND SAMPLE IOCATIONS COLLECTION FREOUENCY OF ANALYSIS
.1. DIRECT RADIATIOND (3) the balance of the stations (Continued) to be placed in special'in- .
- i. -
terest areas such as popu-
.lation centers, nearby resi-dences, schools, and in 1 or 2 areas to serve as control stations.
SECTOR CODE DISTANCE from station (miles)
N CL-37 3.4 N CL-75 0.9 ENE CL-65 2.6 E CL-41 2.4 i S (control) CLell 16 W CL-49 3.5 W CL-74 1.9 WNW CL-64 '2.1 4
CLINTON ~ 5-6 Fev.6-12/89
' CPS-ODCh- _
TABLE 5.1-1 (Continued)
RADIOU3GICAL" ENVIRONMENTAL MONITORING PROGRAM EXPOSURE PATHWAY NUMBER OF REPRESENTATIVE a SAMPLING AND- TYPE AND FREQUENCY AND/OR SAMPLE SAMPLES AND SAMPLE LOCATIONS COLLECTIt' FREOUENCY OF ANALYSIS
- 2. AIRBORNE Radioiodine and Samples from 5 locations: Continuous sampler Radioiodine Canister:
Particulat.es operation with sample I-131 analysis weekly.
- a. 3 samples from close to the collection weekly, or 3 SITE BOUNDARY locations more frequently if in different sectors of the required by dust Particulate Sampler:
highest calculated annual loading. Gross beta radioactivity average ground-level D/Q.
analysis filter change follgw:ing Ganma isotopic analysis" of composite (by location) quarterly.
SECTOR CODE DISTANCE from station (miles)
HNE CL-2 0.7 NE CL-3 0.7 N CL-15 0.9
- b. 1 sample from the vicinity i of a community having the highest calculated annual ;
average ground-level D/Q.
SECTOR CODE DISTAsiCE from station (miles) 3 CL-8 2.2 f t I
CLINTON-1 5-7 Rev.7-2/91 i'
CPS-ODCM TABLE 5.1-1 (Continued 1 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM SAMPLING AND TYPE AND FREQ/ENCY EXPOSURE PATHWAY- . NUMBER OF REPRESENTATIVE a OF ANALYSIS COLLECTION FREOUENCY AND/OR SAMPLE SAMPLES AND SAMPLE LOCATIONS
- 2. AIRBORM6 (Continued)
- c. 1 sample from a control location, as for example 15-30 km (9.3 miles to 18.6 miles) distant and in the least prevalent wind direction c, SECTOR CODE DISTANCE from station (miles).
IG S (control) CL-11
- 3. WATERBORNE e f- 1 sample upstream Composite sample over Gamma isotopic analysis i a. Surface 1 month period 9 monthly. Composite for 1 sample downstream tritium analysis quarterly.
SECTOR CODE DISTANCE from station (m i'. es)
CL-91 6.1 ENE (upstrean)
CL-90 0.4 SE (downstream) r l
5-8 Rev.6-12/89 CLINTON
CPS->ODC(
TABLE 5.1-1 (Continued)
FADIOIDGICAL ENVIRONMENTAL MONITORING PROGRAM NUM3ER OF REPRESENTATIVE SAMPLING AND TYPE AND FREQUENCY EXPOSURE PATHNAY e SAMPLES AND SAMPLE LOCATIONS COLLECTION FREOUENCY OF ANALYSIS AND/OR SAMPLE
- 3. WATERBORNE (Continued)
Samples from 1 or 2 sources, h Quarterly Gamma isotopic" and
- b. Ground tritium analysis only if likely to be affected .
quarterly.
SECTOR CODE DISTANCE from station fmiles)
E CL-12 1.6*
ESE CL-7D 2.3
- Sriple location is in pump station distant from well. Well located i a mile S of plant on the edge of the lake.
1 sample of each of 1 to 3 of Composite sample I-131 onalysis on each
- c. Drinking the nearest water supplies over 2-week period 9 composite when the dose that could be af acted by itr when I-131 analysis calculated for the con-discharge.* is performed, monthly sumption of the water is composite otherwise greater than 1 mrem per year.1 Composite for
- No municipal cr }<ublic drinking water supplies gross beta and gamma isotopic analyses" are taken from Cll: ton Lake or downstream for monthly. Composite for 200 miles. Drinking water for Clinton Power Station is supplied by Clinton Lake. Samples tritium analysis for this drinking water source are required by quarterly.
Table 5.1-4, item 3.
1 sample from a control location **
- Ko control location necessary.
CLINTON-1 5-9 Rev.6-12/89
' CPS-ODCM TABLE 5,1-1 (Continu@d)
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAh' TYPE AND FREQUENCY EXPOSURE PATHWAY . NUMBER OF REPRESENTATIVE a SAMPLING AND AND/OR SAMPLE SAMPLES AND SAMPLE LOCATIONS COLLECTION FREOUENCY OF ANALYSIS
- 3. WATERBORNE (Continued) 1 sample from downstream' area Semiannually Gamma isotopic analysis e
- d. Sediment from with existing or potential seniannually.
shoreline recreational value.
SECTOR CODE DISTANCE from station (milesl i SE CL-7B 2.1
! 4. INGESTION Gamma isotopic e and
- l
] a. Milk Samples from milking animals Semimonthly when
~
in 3 locations within'5-ku a71ma1s are on I-131 analysis semi-distance having the highest pustare, monthly monthly when animals dose potential If there are at u_her times are on pasture; none, then, 1 sasple from monthly at other milking animals in each of 3 times.
- arsas between 5 to 8 km distant from doses are calculated to mb in. greater than 1 mrem per yr.l*
1 *No milking animals within 8 km of the site were identit'ied in the most recent annual land n'se survey.
CLINTON ' 5-10 Rev.6-12/89
CPS-ODC.
TABLE 5.1-1 (Continued)
RADIOIDGICAL ENVIRONMENTAL MONITORING PROGRAM EXPOSURE PATHWAY NUMBER OF REPRESENTATIVE a SAMPLING AND TYPE AND FREQUENCY AND/OR SAMPLE SAMPLES AND SAffPLE LOCATIONS COLLECTION FREOUENCY OF ANALYSIS
- 4. INGESTION (Continued)
- a. Milk 1 sample from milking animals (continued)- at a control location, 15-30 km (9.3 miles to 18.6 miles) distant and in the least
, prevalent wind direction.
~
SECTOR ~ CODE DISTANCE from station (miles)
WSW (control) CL-116 14
- b. Fish and 1 sample each of 3 important Sample in season, or Gamma isotopic analysise Inverte- species (such as bass, semiannually if they on edible portions.
brates crappie, carp, or bluegill) are not seasonal in vicinity of plant dis-charge area. I SECTOR CODE DISTANCE from station ? miles)
! J CL-19 3.4 I sample of same species in 4-areas not influenced by !
plant discharge. ,
e SECTOR CODE DTSTANCE from station (miles)
S (control) CL-105 50 1
l CLINTON-1 -11 Rev.6-12/89
m k
CPS-ODCM TABLE 5.1-1 (Continued)
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM NUMBER OF REPRESENTATIVE SAMPLING AND TYPE AND FREQUENCY EXPOSURE PATHWAY a OF ANALYSIS AND/OR SAMPLE SAMPLES AND SAMPLE LOCATIOUS_ COLLECTION FREOUENCY
- 4. INGESTION (Continued) 1 sample of each principal At time of harvest 3 Gamma isotopic analysis e
- c. Food on edible portion.
Products clasa of food products from any area that is irrigated
- by 1ater in which liquid plant wastes have been discharged.*
- No known usage of Salt Creek wator for irrig;.ation in DeWitt, Logan, Menard, or Cass Counties. This information is checked annually as
! part of the land use survey.
Samples of 3 different kinds Monthly during essma isotopic e and of broad leaf vegetation growing season 1-131 enalysis.
l- ~
(such as lettuce, cabbage, and swiss chard) grown nearest each of two different offsite locations of highest.
predicted annual average ground-level D/Q if milk l sampling is not performed.
- SECTOR CODE DISTANCE from station (miles)
NE CL-115 0.7 N CL-117 0.9 9
CLINTOF 5-12 Rev 2/91
_ _ _ _ _ _ -M -" si
CPS-ODCh_ _
TABLE 5.1-1 (Continued)
RADIOIOGICAL ENVIRONMENTAL MONITORI G PROGRAM EXPOSURE PATI!WAY NUMBER OF REPRESENTATIVE a SAMPLING AND TYPE AND FREQUENCY
, _ AN0/OR SAMPLE SAMPLES AND SAMPLE LOCATIONS COLLECTION FREOUENCY OF ANALYSIS a
- 4. INGESTION I: (Continued)
- c. Food l' sample of each of the similar Monthly during Gamma isotopice and
, Products broad leaf vegetation grown growing season I-331 l-(continued) 15-30 km (9.3 miles to 18.6
' miles). distant in the least >
prevalent wind direction if '
milk sampling is not :
l performed.
SECTOR CODE DISTANCE from station (miles)
SSE (Control) CL-114 12.5 1
l 1
J t
i i
CLINTON-1 5-13 Rev.6-12/89 J
CPS-ODCM TABIE 5.1-1 (Continued)_
RADIOLOGICAL ENVIRol; MENTAL MONITORING PROGRAM TABLE NOTATIONS aRefer to ITUREG-0133, " Preparation of Radiological Effluent Technical Specifications for Nuclear PoWor Plants," October 1978, and to Radiological Assessment Branch Technical Position, Revision 1, November 1979. Deviations are permitted from the required sampling schedule if specimens are unobtainable due to hazardous conditions, seasonal unavailability, malfunction of automatic sampling equipment and other legitimate reasons. If specimens are unobtainable due to sampling equipment malfunction, every effort shall be made to completo corrective action prior to the end of the next sampling period. All deviations from the sampling schedule shall be documented in the Annual Radiological Environmental Operating Report pursuant to Technical Specification 6.9.1.6. It is recognized that, at timos, it may not be possible or practicable to continue to obtain samplee of the media of choice at the most desired location or time. In these
'instancos suitable alternative media and locations may be chosen for the particular pathway in questioa and appropriato substitutions made within 30 days in the radiological environmental monitoring program. Pursuant to Technical Specification 6.9.1.7, identify the cause of the unavailability of samplos for that pathway and identify the new location (s) for obtaining replacement samples in the next Semiannual Radioactive Effluent Release Report and also include in the report a revised figure (s) and table for the OOCH reflecting the now location (s).
bone or more instruments, such as a pressurized ion chamber, for measuring and recording dose rate continuously may be used in place of, or in addition to, integrating dosimeters. For the 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. Film badges shall not be used as dosimeters for measuring direct radiation. The 40 stations is not an absolute number. 'hc number of diz- . radiation monitoring stations at an may be ocean site, reduced according to geograp..ical limitations; e.g.,
some sectors will be over water so that the number of dosimeters may be reduced accordingly. The frequency of analysis or readout for TLD systems will depend upon the characteristics of the specific system used and should be selected to obtain optimum dose information with minimal fading.
cThe purpose of_this sample is to Sbtain background information. If it is not practical to establish control locations in accordance with the distance and wind direction criteria, other sites that provide valid backgiound data may be substituted.
CLINTON-1 5-14 Rev.6-12/89
1 I
cps-ODCM TABLE 5.1.1 (Continued)
RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM TABLE NOTATIONS (Continued) d Airborno particulate sample filters shall be analyzed for gross beta radioactivity 24 hours2.777778e-4 days <br />0.00667 hours <br />3.968254e-5 weeks <br />9.132e-6 months <br /> or more after sampling to allow for radon and thoron daughter decay. If gross beta activity in air particulate samples is greater than ten times the yearly mean of control samples, gamma isotopic analysis shall be performed on the individual samples.
eGamma isotopic analysis means the identification and quantification of gamma-emitting radionuclides that may be attributable to the effluents from the facility.
- fThe " upstream sample" snall be taken at a distance beyond significant influence of the discharge. The " downstream" sample shall be taken in an area beyond but near the mixing zone. " Upstream" samples in an estuary must be taken far enough upstream to be b6 yond the plant influence. Salt water shall be sampled only when the receiving water is utilized for recreational activities.
9A composite sample is one in wh4ch the quantity (aliquot) of liquid samp3.ed is proportional to the quantity of flowing liquid (or time) and in which the method of sampling employed results in a specimen that is representative of the liquid flow. In this program composite sample aliquots shall be collected at time intervals that are very short (e.g., hourly) relative to the compositing period (e.g.,
monthly) in order to assure obtaining a representative sample, h Groundwater samples shall be taken when this source is tapped for drinking or irrigation purposes in areas where the. hydraulic gradient or recharge properties are suitable for contamination.
i The dose shall be calculated for the maximum organ and age group, using the methodology and parameters in Section 2.4.2.
d If harvest occurs nore than once a year, sampling shall be performed during each discrete harvest. If harvest occurs continuously, sampling shall be monthly. Attention shall be paid to including samples of tuborous and root food products.
i l
CLINTON-1 5-15 Rev.6-12/89
CPS-ODCM TABLE 5.1-2 REPORTING ' LEVELS FOR RADIOACTIVITY CONCENTRATIONS IN ENVIRONMENTAL SAMPLES FISH HILK FOOD PRODUCTS-WATER AIRBORNE PARTICULATE 3 ; -
OR GASES (DCi/m ) . (DCi/ka ' wet) (DCi/l) (DCi/ka wet)
ANALYSIS (DCi/1).
H-3 20,000*
30,000 Hn-54 1,C00 t
I 400 10,000
( Fe-59 1,0GO 30,000 Co-58 300' 10,000 f Co-60 20,000 Zn-65 300 Zr-Nb-95 400***
0.9 3 100 I-131 2**
1,000 60 1,000 Cs-134 30 10 20 2,000 70 2,000 Cs-137 50 300 Ba-La-140 200***
If not drinking water pathway
- For drinking water samples. . This is 40 CFR Part 141 value.
exists, a value.of'30,000 pC1/1 may be used.
- If no drinking water pathway exists, a value of 20 pCi/l may be used. 1
)
- Total for parent and daughter 5-l' Rev.6-12/r CLIT 'N-1
CPS %sCM TABLE 5.1-3 a,b DETECTION CAPABILITIES FOR ENVIRONMENTAL SAMPLE ANALYSIS C
LOWER LIMIT OF DETECTION (LLD)
FISH HILK FOOD PRODUCTS SEDIMENT WATER AIRBORNE PARTICULATE 3
(pCi/1) OR GAS (DCi/m ) (DCi/ko. wet) (oCi/l) DCi/ka. wet) (nCJ/ku. dry)
ANALYSIS Gross beta 4 0.01 E-3 2000*
Mn-54 15 130 Fe-59 30 260 ,
1 Co-58,60 15 130 Zn-65 30 260 Zr-95 30 Nb-95 15 0.07 1 60 I-131 1**
0.05 130 15 60 150 Cs-134 15 0.06 150 18 80 180 Cs-137 18 60 60 Ba-140 15 15 La-140
- If no drinking water pathway exists, a value of 3000 pCi/l may be used.
- If no drinking water pathway exists a value of 15 pCi/1 may be used.
CLINTON-1 5-17 Rev.6-12/89 1 - _ _
CPS-CDCM TABLE 5.1-3 (Qpnt_inge_d1 a,b DETECTION FOR EITVIRONMENTAL S AMPLE ANALYSIS TABLE NOTATIu1S aThis list does not mean that only these nuclides are to be considered.
Other peaks that are identifiable, together with those of the above nuclidos, shall also be analy.ed and reported in the Annual Radiological Environmental Operating Report pursuant to Technical Specification 6.9.1.6.
bRequired detection capabilities for thermoluminescent dosimeters used for environmental measuromonts shall be in accordance with the recommendations of Regulatory Guide 4.13, Rr r . 1, July 1977.
cThe LLD is defined, for purposes of these spucificat. ions, as the smallest concentration of radioactive material in a cample that will yield a not 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 measuremant system, which may include radiochemical separation:
4.66sb 1 LLD =
E V -
2.22 -
Y -
exp(-Aat)
Where:
LLD is the "a priori" lower limit of detection as defined above, as picocuries per unit mass or volume, sb is the standard deviation of the background counting rate or of the counting rate of a blank sample as appropriate, as counts per minute, E is the counting efficiency, as counts per disintegration, V is the sample size in units of mass or volume, 2.22 is the number of disintegrations por minute per picocurie, Y is the fractional radiochemical yield, when applicable, A is for the parti,:ular radionuclide (sec~{he radioactive decay constant
), and at for environmental samples is the elapsed time between saeple collection, or end of the sample collection period, and time of counting (soc).
CLINTON-1 5-18 Rev.6-12/89 I
. - . . .- . . . - .-. - . - - . . - - - . - . . ~ . . - - . _ - . . - . _ - - .
CPS-ODCM ,
TABLE 5.1-3 (Continued)
DETECTION CAPABILITIES FOR ENVIRONMENTAL SAMPLE ANALYSISa,b TABLE NOTATIONS (Continued)
Typical values of E, V, Y, and At should be used in the calculation.
It should be recognized that the LLD is defined as an a oriori (before the fact) limit representing the capability of a measurement system and not as an a costeriori (after the fact) limit fc 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 Technical Specification 6.9.1.6.
1 CLINTON-1 5-19 Rev.6-12/89
CPS-ODCM
, Table 5.1-4 ENVIRONMENTAL REPORT (OPERATING LICENSE STAGE)
TABLE 6.1-8 REO_QIREMENTS REQUIRED (L*WPLING REQUIRED TYPES EXPOSURE PATHWAY AND. COLLECTION AND FREQUENCY and/or SAMPLE TYPE FREOLTENCY , OF ANALYSIS
- 1. Direct Radiation Quarterly Gamma dose, quarterly SECTOR CODE DISTANCE from station (milesi NNE CL-2 0.7 NE CL-3 0.7 SW CL-4 0.8 WSW CL-6 0.8 SE CL-7 2.3 E CL-8 2.2
- 2. Airborne Continuous sampler Radiciodine operation with Cannister:
sample collection I-131 analysis weekly, composite weekly.
quarterly.
Particulatq Samoler:
Gross beta
-radioactivity analysis following filter changes.
Gamma isotopic analysis of composite (by' location, quarterly).
SECTOR CODE DISTANCE from station (miles)
W CL-1 1.8 SW CL-4 0.8 iSW CL-6 0.8 SE- CL-7 2.3 CLINTON-1 5-20 Rev.7-2/91
l CPS-CDCM l
Table 5.1-4 (continued)
ENVIRONMENTAL REPORT (OPERATING LICENSE STAGE)
TABLE 6.1-3 REOUIREMENTS REQUIRED SAMPLING REQUIRED TYPES EXPOSURE PATHWAY AND COLLECTION AND FREQUENCY and/or SAMPLE TYPE FREOUENCY OF ANALYSIS
- 3. Surface Drinking composite sample I-131 analysis Water over 2-week period on each composite uhen I-131 analysis for the dose in performed calculated for monthly composite the consumption othe s:ct of the water if greater than 1 r mrom per year.
Composite for gross beta and gamma isotopic analysis monthly.
Composite for tritium analysis quarterly.
) SECTOR gQDE DISTANCE from station (miles)
WNW CL-14 within service building
- 4. Surface Water Monthly grab Gamma isotopic sample composited analysis. Tritium quarterly by analysis on a location, quarterly -
composite.
SECTOR gQDE DISTANCS from station (miles)
ESE CL-9 2.7 ENE CL-10 5.0 SW CL-13 3.6
- 5. Bottom Sediment Semiannual grab Gamma isotopic ,
sample. analysis.
SECTOR CODE DISTANCE from station (miles)
So CL-7C 1.3 ENE CL-10 5.0 CLINTON-1 5-21 Rev.7-2/91
i CPS-ODCM i
Table 5.1-4 (continued)
ENVIRONMENTAL REPORT (OPERATING LICENSE STAGE)
TABLE 6.1-8 REOUIREMENTS REQUIRED SAMPLING REQUIRED = TYPES AND COLLECTION AND FREQUENCY EXPOSURE' PATHWAY OF ANALYSIS and/or SAMPLE TYPE FREOUENCY Semiannual grab Gamma isotopic
- 6. Shoreline Sediment sampl+. analysis.
-SECTOR SQDE DISTANCE from station (miles)_
CL-10 5.0
'ENE
- 7. Slime or aquatic Semiannual grab Gamma isotopic sample. analysis.
vegetation (periphyton)
SECTOR CODE DISTANCE from station (miles)
CL-7C 1.3 SE CL-10 5.0 ENE Every three years Gamma isotopic
- 8. Soil analysis.
grab-sampie, )
SECTOR SQDE DISTANCE from station (milesi_
CL-1 1.8 W 0.7 NNE CL-2 CL-3 0.7
-NE 0.8 SW CL-4 CL-6 0.8 WSW 2.3 SE CL-7 CL-8 2.2 E
CL-11 16 S
CL-94 0.6 E
CLINTON-1 5-22 Rev.7-2/91 4
CPS-ODCM Teble 5.1-4 (continued)
ENVIRONMENTAL REPORT (OPERATING LICENSE STAGE)
TABLE 6.1-8 REOUIREMENTS REQUIRED SA)'9 LING REQUIRED TYPES EXPOSURE PATHWAY AND COLLECTION AND FREQUENCY and/or SAMPLE TYEE FREOUENCY OF ANALYSIS 9.-Ground Water Biveekly I-131 - biweekly Grab Gamma isetopic analysis and Gross beta analysis -
monthly.
Tritium analysis -
quarterly composite of monthly.
SECTOR gqQE DISTANCE from station (miles)
E CF-12 1.6*
ESE CL-7D 2.3
- Sample location is in pump station distant from well. . Hell located 1.0 mile S of plant on edge of lake.
CLINTON-1 5-23 Rev.6-12/89
I CPS-ODCM j I
l I
5.2 Land Use Census - Operation and Surveillance Requirements OPERATION REOUTREMENT 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 2nearest residence and the nearest garden
- of greater than 50 m (500 ft2) producing broad leaf vegetation. For elevated or mixed-mode ,
releases as defined in Regulatory Guide 1.111, Revision 1, July l 1977, the land use consus shall also identify within a distance of 5 '
km (3 miles) the location in each of the 16 meteorologicgl producing sectors of all milk animals and all gardens of greater than 50 m broad leaf vegetation. This requirement applies at all times.
REMEDIAL REOUIREMENT:
- 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 Section 3.5.2.1, identify the 1
new location (s) in the next Semiannual Radioactive Effluent Release Report, pursuant to Technical Specification 6.3.1.7.
- b. With a land use census identifying a location (s) that yields a calculated dose or dose commitment (via the same exposure pathway) 20 percent greater than at a location from which samples are currently being obtained in accordance with l Section 5.1, add the new location (s). to the radiological )
environmental monitoring program within 30 days. The sampling location (s), excluding the control station location, having the lowest calculated dose or dose commitment (s), via the same exposure pathway, may be deleted from this monitoring progran after Octobei 31 of the year in which this land use census was conducted. Pursuant to Technical Specification 6.9.1.7, identify the new location (s) in the next Semiannual Radioactive Effluent Release Report and also include in the report a revised figure (s) und table for this manual reflecting the new location (s).
- Broad leaf vegetation sampling of at least three different kinds of vegetation may be performed at the site boundary in each of two different direction sectors with the highest predicted D/Qs in lieu of the garden census. Specifications for broad leaf vegetation l sampling in Table 5.1-1.4c shall be followed, including analysis of control samples. j i
i CLINTON-1 5-24 Rev.6-12/89
CPS-ODCM SURVETLIMICE REOUTREMENTS ,
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 doot-to-door survey, aerial aurvey, 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 Technical Specification 6.9.1.6.
)
CLINTON-1 5-25 Rev.6-12/89
CPS-ODCM 5.3 INTERLABORATORY COMPARISON PROGRAM All analyses for CPS Radiological Environmental Monitoring Program are performed by Teledyne Isotopes Midwest Laboratories (TIML) located in Northbrook, Illinois.
Teledyne Isotopes Midwest Laboratory (fornerly Hazleton Environmental Sciences) has participated in interlabo.atory comparison (crosscheck) programs since the formulation of its quality control program in December 1971. These programs'have been operated by agencies which supply environmental-type samples (e.g.,
milk or water) containing concentrations of radionuclides known to the issuing agency but not to the participant laboratories. The purpose of such a program is to provide an independent check on the laboratory's analytical procedures and to alert it to any possible problems.
Participant laboratories measure the concentracions of specified radionuclides and report them to the issuing agency. Several months later, the agency reports the known values to the participant laboratories and specifies the range the-results should fall within.
Results consistently higher or lower than the known values and results outside the specified ranges indicate a need to check the instruments or procedcres used.
If the results of a determination in the EPA crosscheck program are outside the control limits specified by the EPA, CPS will require TIML to investigate the cause of the problem and take steps to y correct it. The results of this investigation and corrective action '
shall be included in the Annual Radiological Environmental Operating Report.
Operation and Surveillance Requirements for the Interlaboratory Comparison Program are prescribed in Section 5.3.1 (which follows).
CLINTON-1 5-26 Rev.6-12/89
~ . - - - - . - - .. -. . - - . _.
CPS-ODCM 5.3.1 Interlaboratory Comparison Program - Operation and Surveillance Requiremen_ts OPERATION REOUIREMENT Analyses-shall-be perfo$med on all radioactive materials, supplied as part of an Interlaboratory Comparison Program that has been approved by the. commission, that correspond.to samples required by Table 5.1-1. This requirement applies at all times.
REMEDTAL REOUIREMENT:
- a. ~With analyses not beingLperformed as required above, report the corrective actions taken to prevent a recurrence to the Commission in the Annual Radiological Environmental Cperating-
= Report pursuantito Technical Specification 6.9.1.6.
SURVEILLANCE REOUIREMENTS 5.3.1.1 The Interlaboratory Comparison Program is described in Section 5.3. A summary of the results obtaineo'as part of the above required Interlaboratory Comparison Program shall be included in the Annual Radiological Environmental-Operating Report pursuant to Technical Specification 6.9.1.6.
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CLINTON-1 5-27 Rev.6-12/89 M y --n -
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6.0 BASES FOR OPERATION AND SURVEILLANCE REOUIREMENTS 6.1 General Operation and Surveillance Reauirements The requirements of Sections 1.2 and 1.3 provide general requirements applicable to each of the Operation Requirements and Surveillance Requirements specified within Sections 2.0 through 5.0. .
1.2.1 This requirement is provided to emphasize when each Operation Requirement is applicable and when the associated REMEDIAL REQUIREMENT should be met.
1.2.2 This requirement defines those conditions necessarv to constitute compliance with the terms of an individual Operation Requirement and associated REMEDIAL REQUIREMENT. r 1.3.1 This requirement provides that surveillance activities, will ce necessary to ensure the Operation Requirements are met, performed during the conditions fcr which the Operation Requirements are applicable. Some surveillance activities may be required to be performed without regard to the applicable conditions specified in the associated Operation Requirement.
1.3.2 The provisions of this requirement provide allowable tolarances for performing surveillance activities beyond These those tolerances specified in the nominal surveillance interval.
are necessary to provide operational flexibility because of scheduling and performance considerations. The phrase "at least" ')
associated with a surveillance frequency does not negate this o allowable tolerance; instead, it permits the more frequent performance of surveillance activities.
The tolerance values, taken either individually or consecutively over three test intervals, are sufficiently restrictive to ensure that the reliability associated with the surveillance activity is _
not significantly degraded beyond that obtained from the nominal specified interval.
1.3.3 The provisions of this requirement set forth the criteria for determination of compliance with the OPERABILITY requirements of the Operation Requirements. Under these criteria, equipment, systems, or components are assumed to be OPERABLE if the associated surveillance activities have been satisfactorily performed within the specified time interval. Nothing in this provision is to be construed as defining equipment, systems or components OPERABLE, when such items are found or known to be inoperable although still meeting the Surveillance Requirements.
CLINTON-1 6-1 Rev.6-12/89
___ - - - __-___ D
-CPS-ODCM l- 1.3.4 This requirement ensures that surveillance activities associated with a Operation Requirement have been performed within the specified time interval prior to entry into a specified system operating mode. The intent of this provision is to ensure that surveillance activities have been satisfactorily demonstrated on a current basis as required to meet the OPERABILITY requirements of the Operation Requirement.
Under the terms of this requirement, for example, during initial plant-startup or following extended plant outage, the applicable surveillence activities must be performed within the stated surveillance interval prior to placing or returning the system or equipment into OPERABLE status.
6.2 Monitorina Instrumentation Section 2.7: Radioactive Licuid Effluent Monitorina Instrumentation The radioactive liquid effluent in,strumentation is provided to monitor and control, as applicable, the releases of radioactive materials in liquid effluents during actual or potential releases of liquid effluents. The alarm / trip setpoints for these instruments shall be calculated and adjusted in accordance with the methodology e.nd parameters in this manual to ensure that the alarm / trip will occur prior to exceeding the limits of 10 CFR Part 20. 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.
Section 3,9.1: Offcas Radiation Monitorina InstrumentatioD The OPERABILITY of the radiation monitoring instrumentation ensures that; (1) the radiation levels are continually measured in the areas served by the individual channels; (2) the alarm or automatic action is initiated when the radiation level trip setpoint is exceeded; and (3) sufficient information is available on selected. plant parameters to monitor.and assess these variables following an accident. This capability is consistent with 10 CFR Part 50, Appendix A, General Design Criteria 19, 60, 61, 63 and 64.
CLINTON-1 6-2 Rev.6-12/89
CPS-ODCM Section 3.9.2: Radioactive Gaseous Effluent Monitorina jnptrumentation The radioactive gaseous-effluent instrumentation as provided to monitor and control, as applicable, the release 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 this manual to ensure that the alarm / trip will occur prior to exceeding the limits of 10 CFR Part
- 20. 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 CFK Part 50. The sensitivity of any noble gas activity monitors used to.show compliance with the gaseous effluent releaserequirementsofSectiong.S.1shallbesuchthat concentrations as low as 1 x 10~ gCi/ml are measurable.
6.3 Radioactive Effluenta
.6.3.1 Licuid Effluents Section-2.3.1: Licuid Effluent Concentration This requirement is provided to enrure that the concentration of radioactive' materials released in liquid waste effluents to UNRESTRICTED AREAS will be less than the concentration levels This j specified in 10 CFR Part 20, Appendix B, Table II, Column 2.
limitation provides. additional assurance that the le"els of radioactive materials in bodies of water in UNRESTRICTED AREAS will result in exposures within (1) the Section II.A design objectives of Appondix I, 10 CFR Part 50, to a MEMBER OF THE PUBLIC and (2) the limits of 10 CFR Part 20.106(e) to the population. The concentration limit for dissolved or entrained noble gases is based upon the assumption that Xe-135 is the controlling radioisotope and its MPC in air (submersion) was converted to an equivalent concentration in water using the methods described in International Ccmmission on Radiological Protection-(ICRP) Publication 2.
This requirement applies to the release of radioactive materials in liquid effluents from the site.
The required detaction capabilities for radioactive materials in liquid waste samples are tabulated in terms of the lower limits of detection (LLDs). Detailed discussion of the LLD, and other detection limits can be-found in Currie, L. A., " Lower Limit of Detection: Definition and Elaboration cf a Proposed Pcsition for Radiological Effluent and Environmental Measurements," NUREJ/CR-4007 (September 1984), and in the RASL Procedures Manuel, HASL-300 (revised annually).
CLINTON-1 6-3 Rev.6-12/89
CPS-ODCM i l
l Section 2.4.1: 10CFR50. Aopendix I Release Rate Limits This requirement is provided to implement the requirements of Sections II.A, III.A and IV.A of Appendix I, 10 CFR Part 50. The Limiting Condition for Operation implements the guides set forth in Section II.A of Appendix I. The ACTION statements provide the required operating flexibility and at the same time implement the guides Fot forth in Saction IV.A of Appendix I to assure that the releases of radioactive material in liquid effluents to UNRESTRICTED AREAS will be kept "as low as is reasonably achie"Phle." Also, for fresh water sites with drinking water supplies that can be potentially affected by plant cperations, there is reasonable assurance that the operation of the facility will not result in radionuclide concentrations in the finished drinking water that are in excess of the requirements of 40 CFR Part 141. The dose calculation methodology and parameters in this manual implement the requirements in Section III.A of Appendix I that conformance with the guides of Appendix I be shown by calculational procedures basad on models and data, such that the actual exposure of a MEMBER OF ".HE PUBLIC through appropriate pathways is unlikely to be substantially underestimated.- The equaulons specified in this manual for calculating the doses due to the actual release rates of radioactive materials in liquid effluents are consistent with the methodology provided in Regulatory Guide 1.109, " Calculation of Annual Doses to Man from Routine Releases of Reactor Effluents for the P'npose of Evaluating Compliance with 10 CFR Part 50, Appendix I," Revision 1,
) October 1977 and Regulatory Guide 1.113, " Estimating Aquatic Dispersien of Effluents from Accidental and Routine Reactor Releases for the Purpose of Implcmenting Appendix I," Lpril 1977.
This requirement applies to the release of radioactive materials in liquid ef.tluents from the one reactor unit on the site.
Section 2.5.1: Licuid Radwaste Treatment System The OPERABILITY-of the liquid radwaste treatment system ensures that this system will be available for use whenever. liquid effluents require treatment prior to release to the environment. The requirements that the appropriate portions of this system be used when specified provides assurance that the releases radioactive materials in liquid effluents will be kept "as low as is reasonably achievable." This specification implements the requirements of 10 .
CFR Part 50.36a, General Design Criterion 60 of Appendix A to 10 CFR Part 50 and the design objective given in Section II.D of Appendix I to 10 CFR Part 50. The specified limits governing the use of appropriate portions of the liquid rcdwaste treatment system were specified as a suitable fraction of the dose design objectives set forth in Section II.A of Appendix I, 10 CFR Part 50, for liquid effluents.
This requirement applies to the release of radioactive materials in liquid effluents from the one reactor unit on the site.
l l
l CLINTON-1 6-4 Rev.6-12/89 i
CPS-ODCM 6.3.2 Gasecus_Fffluents 3 S_ection 323 1: 10CFR20 Release Rate Limits ,
This requirement is provided 'o ensure that the dose at any time at and beyond the SITE BOUNDAR', from gaseous effluents from all units on the site will be within L;e annual dose limits of 10 CFR Part 20 to UNRESTRICTED AREAS. The annual dose limits are the doses associated with the concentrations of 10 CFR Part 20, 7.ppendix B, Table II, Column 1. These limits provide reasonable assurance that radioactive material discharged in gaseous effluents will not result in the exposure of a MEMBER OF THE PUBLIC in an UNRESTRICTED AREA, either within or outside the S1TE BOUNDARY, to annual average concentrations exceeding the limits specified in Appendix B, Table II of 10 CFR Part 20 (10 CFR Part 20.106(b)). For MEMBERS OF THE _
PUBLIC who may at times be within the SITE BOUNDARY, the occupancy of that MEMBER OF THE FLBLIC will usually be suf ficiently low to compensate for any increase in the atmospheric diffusion factor above that for the SITE BOUNDARY. Examples of such MEMDERS OF THE PUBLIC, with the appropriate occupancy factors. Phall be given in this manual. Doses for such MEMBERS OF THE P(3' 20 are provided in the Semiannual Radioactive Effluent Release RM ort. The specified release rate limits restrict, at all times, the warresponding gamma and beta dose rates above background to a MEMBER OF THE PUBLIC at or beyond the SITE BOUNDARY to less than or equal to 500 mrom/ year to the whole body or to less than or equal to 3000 mrem / year to the skin. These release rate limits also restrict, at all times, the '
corresponding' thyroid dosa rate above background to a child via the inhalation pathway to less than or equal to 1500 mrem / year.
This requirement applies to the release of radioactive materials in gaseous effluents from the one reactor unit on the site.
The required detection capabilities for radioactive material in _
gaseous waste samples are tabulated in iarms of the lower limits of detection (LLDs). 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), and in the RASL Procedures Manual, HASL-300 (revised annually).
Section 3.5.1: Noble Gas Dose This requirement is provided to implement the requirements of The Sections II.B, III.A and IV.A of Appendix I, 10 CFR Part 50.
Limiting Condition for Operation implements the guides set forth in Section II.B of Appendix I. The ACTION statements provide the required operating flexibility and at the same time implement the guides set inrth in Section IV.A of Appendix I to assure that the CLINTON-1 6-5 Rev.6-12/89 f
CPS-ODCM 1
releases of radioactive material in gaseous effluents to UNRESTRICTED AREAS will be kept "aa low as is reasonably achievabla." The Surveillance Requirements implement the requiraments in Section III. A of Appendix I that conformance with the guides of Appendix I be shown by calculational procedures based en models and data such that the actual exposure cf a MEMBER OF THE PUBLIC through appropriate pathways is unlikely to be substantially underestimated. The dose calculation methodology and parameters established in this manual for calculating the doces due to the actual release rates for radioactive noble gases in gaseous effluents are consistent with the methodology provided in Regulatory Guide 1.109, " Calculation of' Annual Doses to Man from Routine Releases of Reactor Ef fluents for the Purpose of Evaluating Compliance with 10 CFR Part 50, Appendix I," Revision 1, October 19 P! c-4 Regulatory Guide 1.111, " Methods for Estimating Atmospheric Transport and Dispersion of Gaseous Effluents in Routine Releactu '
from Light-Water Cooled Reactors," Revision 1, July 1977. Thi equations in this manual for determining the air doces at and anyond '
the SITE BOUNDARY are based upon real time atmospheric conditions.
This requirement applies to the release of radioactive materials in gaseous effluents from the site.
Section 3.5.2: Todine-131. Iodine-133. Tritium, and Radionuclides in Particulate Form This requirement is provided to implement the requirements of i Sections II.C, III.A and IV.A of Appendix I, 10 CFR Part 50. The Limiting Conditions for Operation are the guides set forth in Section II.C of Appendix I. The ACTION statements provide the required operating flexibility and at the same time implement the guides set forth in Section IV..A of Appendix I to assure that the releases of radioactive materials in gaseous effluents to UNRESTRICTED AREAS will be kept "as low as is reasonably ~
achievable." The calculational methods specified in the Surveillance Requirements implement the requirements in Section III.A of Appendix I that conformance with the guides of Appendix I be shown by calculational procedures based on models and data, such that the actual exposure of a MEMBER OF THE PUBLIC through appropriate pathways is unlikely to be substantially underestimated.
The 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 Releanes from Light-Water-Cooled Reactors," Revision 1, July 1977. These equations also provide for determining the actual doses based upon the real time atmospheric conditions. The release rate specitications for '+ dine-131, tritium, and radionuclides in particulate form wiu.. half lives CLINTON-1 6-6 Rev.6-12/89 l
' CPS-ODCM l
greater than 8 days are dependent upon the existing radionuclide
-pathways to man in the areas at and beyond the SITE BOUNDARY. The pathways that were examined in the development of these calculations were: 1) individual inhalation of airborne radionuclides, 2) deposition-of radionuclides onto green leafy vegetation with subsequent consumption by man, 3). deposition onto grassy areas where milk animals and meat producing animals graze with consumption of the milk and meat by man, and 4) deposition on the ground with subsequent exposure of man.
This requirement applies to the release of radioactive materials in gascous effluents from one reactor unit on the site.
Sections 3.6 and 3.7: Gaseous Radwaste (Offaasi Treatment and VentilatinD Exhaust Treatment System The OPERABILITY of the WASTE GAS HOLDUP 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 offluents will be kept "as low as is reasonably achievable."
This requirement implements the requirements of 10 CFR Part 50.36a, General Design Criterion 60 of Appendix A to 10 CFR Part 50 and the design-objectives-given in Section II.D of Appendix 1 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 ,
design objectives set forth in Section II.B and II.C of Appendix I, 19 CFR Part 50, for gaseous effluents.
This requirement-applies to the release of radioactive materials in gaseous affluents from the one reactor unit on the site.
6.3.3 Total Dose Section 4.1: Total Dose This requirement is provided to meet the dose limitations of 40 CFR Part 190 that have been incorporated into 10 CFR Part 20 by 46 FR 18525. The' requirement requires the preparation and submittal of a Special Report whenever the calculated doses from plant generated radioactive affluents and direct Ir.diation exceed 25 mrems to the total body or any organ, except the tnyruid, which shall ee limited to less than or equal to 75 mrems. For s1Les containing tp to 4 reactors, it is highly unlikely that the resultant dose to a MEMBER OF THE PUBLIC will exceed the dose limits of 40 CFR Part 190 if the individuti reactors remain within twice the dose .; sign objectives of Appendix I, and if direct radiation doses from the reactor units and outside storage tanks are kept small. The Special Report will describe a course of action that should result in the limitation of the' annual dose to a MEMBER OF THE PUBLIC to within the 40 CFR Part 190 limits. For the purposes of the Special Report, it may be l
CLINTON-1 6-7 Rev.6-12/89
CPS-ODCM assumed that the dose commitment to the MEMBER OF THE PUBLIC from other uranium fuel cycles 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 Psic 190, the Special Report with a requent for a variance (provide.d the release conditions resulting in violation of 40 CPR Pert 190 have not already been corrected), in accordance with the provisions of 40 CFR Part 190.11 and 10 CFR Part 20.405c, 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 dosc limitation of 10 CFR Part 20, as addressed in Sections 2.3 and 3.4. 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.
6.4 Radiological Environmental Monitorina
,section 5.1: Monitorine Procram The radiological environmental monitoring program required by this requirement provides representative measurements of radiation and of radioactive materials in those exposure pathways and for those radionuclides that lead to the highest potential radiation exposures of MEMBERS OF THE FUBLIC resulting from-the station operation. This
) monitoring program implementsSection IV.B.2 of Appendix I to 10 CFR Part 50 and thereby supplements the radiological effluent monitoring program by verifying that the measurable concentrations of radioactive materials and levels of radiation are not higher than expected on the basis of the effluent measurements and the modeling of the environmental exposure pathways. Guidance for this monitoring program is provided by the Kadiological Assessment Branch Technical Position on Environmental Monitoring, Revision 1, November 1979. The initially specified Lohitoring program will be effective for at least the first three years of commercial operation.
Following this period, program changes may be initiated based on operational experience.
The required detection capabilities for environmental sample analyses are tabulated in terms of the lower limits of detection (LLDs). The LLDs required by Table 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 oriori (before the. fact) limit representing the capability of a measurement system and noc as an a Epsteriqri (after the fact) limit for a particular measurement.
i CLINTON-1 6-8 Rev.6-12/89 l
CPS-ODCM l
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), and in the HASL Procedures Manual, HASL-300 (revised annually).
Section 5. 2 (_J3nd Use Census This requi' cement 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 land use census shall be performed using the best information available (e.g., a door-to-door survey, from aerial surveys, questionaire, or from consulting with 1ccal agricultural authorities). This census -
satisfies the requirements of Section IV.B.3 of Appendix I to 10 CFR 2 Part 50. Restricting the census to gardens of greater than 50 m provides assurance that significant exposure pathways via leafy vegetables will be identified and monitored since a garden of this size is the minimum required to produce the quantity (26 kg/ year) of leafy ' egetables 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 s and (2) broad leaf vegetation (i.e.,2,imilar to lettuce and cabbage) a' vegetation yield of 2 kg/m Section 5.3.1: Interlaboratorv Comnarison Procram ,
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 material in environmental sample matrices are performed as part of the quality assurance program for environmental monitoring in order to demonstrate that the results are valid for the purposes of _
Section IV.B.2 of Appendix I to 10 CFR Part 50.
i CLINTON-1 6-9 Rev.6-12/89
CP3-ODCM 7.0 Renortino Recuirements 7.1 Annual Radiolecical Environmental Oneratino Renort Routine Radiological Environmental Operat!ng Reports covering the operation of the unit during the previous calendar year shall be submitted pric. to '. fay 1 of each year pursuant to Technical Specification 6.s.l.6.
The Annual Radiological Environmental Operating Reports shall include the follcwing information:
l '. 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.
- 2. The results of land use. censuses required by Section 5.2.
- 3. 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 Tables and Figures-in this manual, 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.
- 4. A summary description of_the radiological environmental monitoring program.
- 5. At least two legible maps
- covering all sample locations keyed to a table giving distances and directions from the HVAC stack.
- 6. The results of licensee participation in the Interlaboratory Comparison Program, required by Section 5.3.1.
- 7. Discussion of all deviations from the sampling schedole of Table 5.1-1.
One map shall cover stations near the site boundary and a second map shall include the more distant stations.
) i 1
CLINTON-1 7-1 Rev.6-12/89
)
I
- 8. Discussion of all analysis in which the LLD required by Table 5.1-3 was not achievable.- ,
7.2 semiannual Radioactive Effluent Release Recort Routine Radioactive Effluent Release Reports covering the operation of the-unit during the previous 6 months of operation shall be submitted within 60 days after January 1 and July 1 of each year pursuant to Technical Specification 6.9.1.7.
The Semiannual Radioactive Release Report shall include the following information:
- 1. 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 3 additional categories: class of solid wastes (as defined by 10 CFR Part 61), type of container (e.g., LSA, Type A,_ Type B, Large Quantity), and SOLIDIFICATION agent or absorbent (e.g.,
cement, urea formaldehyde).
- 2. The following information for each class of solid waste (as i defined by 10 CFR Part 61) shipped offsite during the report period:
- a. Total container volume,
- b. Total curie quantity (specify whether determined by measurement or estimate),
- c. Principal radionuclides (specify whetner determined by measurement or estimate),
- d. Source of waste and processing employed (e.g.,
dewatered spent resin, compacted dry waste, evaporator bottoms),
- 3. A list and description of unplannad releases from th'e site to UNRESTRICTED AREAS of radioactive materials in gaseous and liquid effluents made during the reporting period.
I CLINTON-1 7-2 Rev.8-7/91 1
I l
CPS-ODCM
- 4. A listing of new locations for dose calculations and/or environmental monitoring identified by the land use census pursuant to Section 5.2.
- 5. Changes to the ODCM pursuant to Technical Specification 6.14.
- 6. Major changes to gadioactive liquid, gaseous, and solid waste treatment systems . The discussion of each change shall contain:**
- a. A summary of the evaluation that led to the determination that the change could be made in accordance with 10 CFR Part 59.59.
- b. Sufficient detailed information to totally support the reason for the change without benefit of additional or supplemental information;
- c. A detailed description of the equipment, components and processes involved and the interfaces with other plant systems;
- d. 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; i
- e. An evaluation of the change, which shows the expected minimum 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;
- f. A comparison of the predicted releases of radioactive materials, in liquid and gaseous effluents and in solid waste, to the actual releases for the period prior to when the changes are to be made;
- g. An estimate of the exposure to plant operating personnel as a result of the change; and
- h. Documentation of the fact that the change was reviewed and found acceptable by the FRG.
- Licensees may choose to submit the information called for in this requirement as part of its annual USAR update.
o* Changes described by this requirement shall become effective upon review by the FRG.
CLINTON-1 7-3 Rev.6-12/89
CPS-ODCM The Semiannual Radioactive Effluent Release Report to be submitted within 60 days af ter January 1 of each year shall also include the folicwing information:
- 1. An annual cammary 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 distributigns of wind speed, wind direction, and atmospheric stability
- 2. As assessment of the radiation doses due to the radioactive liquid and gaseous affluents released from the unit or station i during the previous calendar year. -
- 3. 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 (Figures 2.1-1 and 3.1-1) 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 releasa of radioactive materials in gaseous effluents, as determined by sampling frequency and measurements, shCil be used for determining the gaseous pathway doses. The assessment of radiation doses shall be performed in accordance with the methodology and ;
parameters in this manual.
- 4. An assessment of radiation doses to the likely mest exposed MEMBER OF THE PUBLIC from reactor releases and other nearby uranium fuel cycle sources, including doses from primary effluent pathways and direct radiation, for the previous calendar year to show conformance with 40 CFR Part 190, .
Environmental Radiation Protection Standards for Nuclear Power Operation.
Acceptable methods for calculating the dose contributica from liquid and gaseous effluents are given in Regulatory Guide 1.109, Rev. 1, October 1977.
- *In lieu of submission with the first half year 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.
CLINTON-1 7-4 Rev.6-12/89 9
CPS-ODCM l
l 8.0 ADESTMENT OF THE CPS ODCM METHODOLOGY Consistent with the NRC Commissioners' opinion on 10CFR50 Appendix I dated April 30, 197S, CPS will use environs monitoring data to improve dose calculational models and to request CPS ODCM changes on the basis of such operating experience data. Such adjustments are recognized as being especially important for the radiciodine-milk pathway where conservative regulatory guide assumptions have been made. By itsing envirens mt .itoring data, uncertainties associated with plume behavior, radiolodine chemical form, deposition and retention of forages, and milk consumption patterns may be circumvented or reduced.
)
CLINTON-1 8-1 Rev.6-12/89
1
! CPS-ODCM 9.0 ATMOSPHERIC TRANSPORT AND DISPERSION MODEL 9.1 Introduction The atmospheric transport and dispersion model used by Illinois Power Company is a straight-line, sector-averaged Gaussian model designed to estimate average relative concentrations at various receptor points. The model was developed in accordance with routine release analysis procedures specified by Regulatory Guide 1.111 (Revision 1 July 1977), Section C.1.c " Constant Mean Wind Direction Models".
All meteorolosical and dose calculations prescribed in this manual are based on meteorological data concurrent with the ~
time of release. Near-real time meteorological data processing is described in Section 9.2 9.2 Concurrent Meteorolooical Data Processinc Meteorological data is acquired and processed through a model which utilizes bi-level hourly meteorological tower data or single level joint frequency data to perform the required analysis. Three distinct release modes are treated: elevated, ground and mixed. A set of five output arrays ar generated for each dose receptor location as follous:
5
- Relative undecayed, undepleted plume concentration (X/Q)
Relative decayed and depleted radiciodine and particulate concentration (D2DPXQ)
Relative decayed noble gas concentration (D1XQ) .
- Relative particulate and radiciodine deposition (D/Q)
- Standard deviations of the undecayed, undepleted plume concentrations Since the Regulatory Guide 1.111 depletion and deposition curves are defined only within the range encompassing 100 to 1 200,000 meters, analysis results are not considered valid outside this range. The following sections describe the c calculations performed by the transport and dispersion model for a one hour time interval.
CLINTON-1 9-1 Rev.6-12/89
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s . CPS-ODCMi 9.2.1 -Determination of'Pascuill Stability Class The Pasquill Stability Class-is_ determined by categorizing the temperature gradient, AT, into one of-several ranges-between_-0.900 and 0.900 *C/ meter
-according.to_the following equation:
ATE = TU -T-.L , 'C/ meter (1)
Hg -HL where Tu =' Meteorological (met) tower upper level temperature,C-TL =_ Meteorological tower lower level' temperature, *C Hg.=-Meteorological tower upper level instrumentation height-L= 60 meters HL = Meteorological tower _ level instrumentation height
= '10 meters
.aT iIs then classified according to the following 1- -scheme:
Pascuill' Stability -Definino Condition A~(Extremely Unstable) -0. 900 < AT s-0. 019 B- -0.019 < AT s-0. 017 C .
-0. 017 - < AT _ s-0. 015
-n~(Neutral) -0 . 015 ' ' < AT s-0. 0 0 5 a -0. 005 < AT $ 0. 015
-F 0. 015 < aT $ 0. 04 0
-G (Extremely-Stable)-
- 0. 04 0 - < AT 's ' O . 9 0 0 Invalid AT s-0. 900 - or; 4T> 0. 900 9.2.2 -Calculation of Stack Heicht Wind'Soeed-The wind speed'at the releaseLpoint (HVAC Exhaust Stack' orLStandby. Gas Treatment _ System Exhaust Stack)1 height, STACWS, is calculated:using-the expressions:
STACWS = WSPU -(STACKH/H U ) P, meter /sec (2)
P-= log (WSPL/WSPg) , dimensionless (3) log (HL/Hg) 1' 1)--
CLINTON-1: 9-2 Rev.6-12/89
CPS-ODCM b u . s::e WSPy = Upper met tower level wind speed, <
meter /sec WSP L = Lower met tower level wind speed, meter /sec STACKH = Physical release point stack height P = Wind power law exponent, dimensionless All other parameters are as defined for equation (1).
9.2 3 Determination of Releaqs Mode and the Entrainment goefficient The wode of release can be elsvated, ground or mixed; The the latter being a combinatian of the first two.
mode of release, as well as an entrainment coefficient, TCORR, are determined f: om the stack height, STACH, building height, BLDGHT stack exit velocity, EXITV, e
and the wind espeed .'.t 2 9 stack height, STACWS.
For effluents exhausted from release points that are higher than twice the height of adjacent solid structures, i STACKH > 2(BLDGHT) , TCORR = 0.0 (4) the release is considered completely elevated and the entrainment coefficient is zero. For effluents released from points less than the height of adjacent solid structures, a ground-level release is assumed
~
STACKH < BLDGHT , TCORR = 1.0 (5) and the entrainment coefficient is unity. For ,
effluents released from pr.nts or vents at the level of, or above, adjacent solid structures, but lower than elevated release points, 2(BLDGHT) > STACKH > BLDGTJ (6)
Y.
the release is treated as elevated, ground or mixed i according to the following relationships:
TCORR = 0.00 if EXITV >5(STACWS) (7)
ELEVATEQ:
GROUND: TCORR = 1.0 if EXITV < STACWS (8)
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CPS-ODCM ,
MIXED: TCORR = 0.30-0.06(EXITV/STACWS) if (9) ;
5(STACWS) 1 EXITV > 1.5 (STACWS) 7 ICORR = 2.58-1.58(EXITV/STACWS) if (10) 1.5(STACWS) 2 EXITV 2 (STACWS)
In the mixed mode, the release is considered to occur as an elevated release 100(1-TCORR) percent of the time and as a ground release 100(TCORR) percent of the time.
Each of these cases are than evaluated separately and ;
the conc 2ntration X/Q ca.'.culated according to the i fraction of the time et- . release occurs.
9.2.4 Calculation of Vertical Standard Deviation ,
The vertical plume spread (vertical standard deviation), a=, is a function of the distance from the release point to the reception point for a given Pasquill stability class. The numerical value of "z if obtained by a polynominal fitting equation which '
simulates Figure 1 of Keyulatory Guide 1.111:
o r " 10(A + B log (X) +C (log (x)) 23 , meter (11) where X = b)suance to a specific receptor, kilometer
)
A,B,C = Empirical factors which vary by stability c? ass, determined by fitting polynominal equations to the Regulatory Guide 1.111 Figure 1 curves, dimensionless Emnirical Factors Used in Ecuation (111 Pasouill Clagg & H g A 2.79166 2.69043 1.07483 B 2.11394 1.47930 0.40676 C 1.81954 0.88317 -0.06101 D 1.51851 0.74130 -0.08699 E 1.36173 0.68570 -0.11956 F 1.14613 0.66066 -0.12363 G 1.14613 0.66066 -0.12363 Additionally, an optional value called the " mixing height lid" may ao specified which limits the value of og to be no greater than this value, t
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CLIllYON-1 9-4 Rev.7-2/91
-.-,r -- n-- 4 ,,-~ng- , , .w e, ,. - , ,-------w . . , - , , , . , - .y-,,-,e - , , = a . - n
CPS-ODCM 9.2.5 Calculation _of the Buildina Wake Correction t For ground-based and mixed-mode releases, an adjustment is made in the calculation of X/Q that takes into consideration initial mixing of the effluent plume within the building wake. This adjustment is an additional factor added in quadrature to the vertical plume spread equation (11):
E m (af+0.5(DLDGHT)2, 7 )% (12) with the requirement that Eg is restricted to values Ez $ (3) (az) .
9.2.6 _ Calculation of Momentum Plume Rise For elevated or mixed-mode releases only, the amount of plume rise due to the initial vertical momentum For Pasquill of the exhausted effluent, aH, is calculated.
stability classes A,B,C and D, aH is calculated p' .
section 9.2.6.1; for classes E,P and G, section 9.2.6.2 is used.
9.2.6.1 AH For Pasmlill Class A.B.C and D AH is calculated using both equations (13) "
j and (14) and the minimum valuo is selected In addition, when the vertical for use.
exit velocity, EXITV, is less than 1.5 times the horizontal windspeed, STACWS, a downwash correct' ion is subtracted from equation (13) per equation (15).
(13) aH 1 = 1.44 (STACD) (EXITV/STACWS) 2/3 (X/STACD)1/3-DOWNWASH, meter AH3 = 3.0 (STACD) (EXITV/STACWS) , meter (14)
DOWNWASH = 3. 0 (STACD) (1. 5-EXITV/STACW3) , meter (15) where STACD = Internal release point stack diameter
= 3.77 meters (HVAC Exhaust Stack) 0.44 meters (SGTS Exhaust Stack) 3 EXITV = Stack exit velocity, meter /second All other parameters are as defined previcualy.
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CPS-CDCM 9.2.6.2 AH For Pasauill Class E.F and G AH is determined by selecting the minimum value calculated by equations (13) and (14) above and equatiens (16) and (17) belovt AH3
- 4. 0 ( (0. 5 (EXITV) (STACD) ) 2/S)k, meter (16)
AH4 = 1.5 ( (0. 5 (EXITV) (STACD) ) 2/STACWS)1/3(S)-1/6, (17) meter where S = Restoring acceleration per unit vertical displacement for adiabatic motion, sec -2
= 8.70E-04 (E stability)
= 1.75E-03 (F stability)
= 2.45E-03 (G stability)
All other parameters are as defined in section 9.2.6.1.
9.2.7 Calculation of the Effective Plume Reicht The effective plume height, H, is determined using section '
9.2.6 results for the momentum plume rise, AH, and the terrain height, TERAIN:
) H = STACKH + AH - TERAIN , meter (18) where TERAIN = Difference between the plant base height above mean sea level (MSL) and the receptor point height above MSL, meter 20.0
-CLINTON-1 9-6 Rev.6-12/89 i
CPS-ODCM 9.2.8 Determination of Affected Sectors i The wind direction for the hour determined which sector will be affected. Sectors are 22.5' arcs and are classified according to the following scheme:
Sector Compass Wind Direction (WD)
Number Direction 1 N 0.0' < WD < 11.25' or 348.75* 1 WD < 360.00*
2 NNE 11.25' $ WD < 33.75' 3 NE 33.75* 5 WD < 56.25' 4 ENE 56.25' $ WD < 78.25' 5 E 78.75' 1 WD < 101.25' 6 ESE 101.25' s WD < 123.75' 7 SE 123.75' $ WD < 146.25' 8 SSE 146.2S' $ WD < 168.75' 9 S 168.25' s WD < 191.25' 10 SSW 191.25' s WD < 213.75' 11 SW 213.75' s WD < 236.25' 12 WSW
- 236.25' s WD < 258.75' 13 W 258.75* $ WD < 281.25*
14 WNW 281.75' $ WD < 303.75' 15 NW 303.75# 5 WD < 326.25' 16 NNW 326.25' $ WD < 348.75' For elevated releases, the wind direction at the upper met tower level is used; ground releases follow the direction of the wind at the lower met tower level. For mixed-mode releases, two X/Q calculations are performed: one for each of the two met tower levels. If the wind direction is the sane at both levels, the resulting X/Q will be summed into the same sectort otherwise, the X/Q will be summed into the appropriate sectors. During periods of calm wind, the wind speed is set at one-half the anemometer threshold value and assigned the direction of the previous hour.
9.2.9 Calculation of Denletion and Deposition Factors The depletion, DPF, and deposition, DPSF, factors are calculated using the curves provided by Regulatory Guide 1.111. Actual values are calculated using polynomial equations developed to simulate the Regulatory Guido curves.
Both the DPF and DPSF calculations depend on the effective plume height, H, the stability class, S, and the distance, X, to the receptor. i 1CLINTON-1 9-7 Rev.6-12/89 v -,. . - - - . . . -_ . . - _ _ _
CPS-ODCM The Regulatory Guide 1.111 curves represent plumes that are 100, 60, 30, and 0 (ground-level) meters above the ground.
For plumes between 0 and 15 meters above the ground, the model uses the ground-level release graphs; for those between 15 and 45 meters, it uses the 30 meter curves; between 45 and 80 motors above the ground, it uses the 60 meter curves; and for those greater than 80 meters above the ground, it uses the 100 meter curves. The model assumes that, after full plume rise is achieved, the plume cannot get higher from the ground. The derivation of these curves assumed no change in terrain height with downwind distance. Since topcgraphy does change 'ith distance, and likewise the vertical distance between the plume centerline and the ground, it is necessary to read from_more than one depletion or deposition curvo of Regulatory Guide 1.111 as the plume travels with distance.
9.2.9.1 DPF Calculation The effective plume height, H, is categorized into one of four J-ranges according to the following scheme:
Plume Heicht (meters) J Value 0 $ H s 15 5 15 < H s 45 6 45 < H s 80 7 H > 80 8
)
Similarly, the stability class is categorized into one of three S-ranges as follows:
Stability Class S Value A, B, C 1 D 2 E, F, G 3 I
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The (SJ)-product is then calculated and an (A) value determined at the receptor location X according to the following scheme (where no A value is given, DPF=1.0):
S*J Value X A DPF ,
i 5 X < 100 1.0 ,
X 2 100 A=1 calculated 6 X < 200 1.0 X 2 200 A=5 calculated 7 X < 300 1.0 X 2 300 A - 17 calculated 8 X < 600 1.0 X 2 600 A = 29 calculated 10 all X 1.0 12 X < 400 1.0 X 2 400 A=9 calculated 14 X < 1000 1.0 ,
X 2 1000 A = 21 calculated 15 all X 1.0 16 X < 1700 1.0 X 2 1700 A = 33 calculated 18 X < 6000 1.0 X 2 6000 A = 13 calculated 21 X < 60,000 1.0 X 2 60,000 A = 25 calculated 24 all X 1.0 i DPF is calculated using the value for A and equations (19) and (20):
DPF = B(A) + B(A + 1)d + B(A + 2)d2 + b(A + 3)d3 (19) d = log (X) (20) 1
- CLINTON-1 9-9 Rev.6-12/89
- , , -.m , , - ~ , - - - , , , -
CPS-CDCM The corresponding values for the B(A), E liA + 1), B(A +
- 2) and B(A + 3) terms are as follows: d B(1) = .788234 B(19) = .426473 B(2) = .207198 B(20) = -0.0471767 B(3) = .0563034 B(21) = .615442 B(4) = .0 B(22) = .317258 B(5) = 2.59508 B(23) = .0631839 B(6) = -1.43610 B(24) = .0 B(7) = .433300 B(25) = ~6.89581 B(8) = .0466221 B(26) = 3.37961 '
B(9) = 1.507264 B(27) = .361582 B(10) = .2745668 B(28) = .0 B(11) = .0556577 B(29) = 3.58532 B(12) = .007670194 B(30) = -2.21101 -
B(13) = -18.01858857 B(31) = .642613 B(14) = 12.755137 B(32) = .0651465 B(15) = ~2.7658938 B(33) = .234274 B(16) = .19103896 B(34) = .512656 B(17) = 2.47756 B(35) = .0857995
- B(18) = 1.36010 B(36) = .0 9.2.9.2 DPSF Calculations Using the same (SJ) and X values determined in section 9.2.9.1, a corresponding C value is defined according to the following scheme (where no C value is given, '
) DPSF = 0):
S*J Value X C DPSF ,
5 X < 100 0 X 2 100 C=1 calculated 6 X < 100 0 -
X 2 100 C=8 calculated 7 X< 100 0 X 2 100 C = 29 calculated 8 X < 100 0 X 2 Iv0 C = 50 calculated 10 al? X 0 12 X < 100 0 X 2 100 C = 15 calculated 14 X < 120 0 X 2 120 C = 36 calculated 15 all X 0 16 X < 210 0 X 2 210 C = 57 calculated 18 X < 2900 0 X 2 2900 C = 22 calculated 21 X < 26,000 0 X 2 26,000 C = 43 calculated 24 all X 0
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CLINTON-1 9-10 Rev.6-12/89
CPS-ODCM I
DPSF is calculated using the value for C and equations )
(20), (21), and (22):
DPSF = 10Y /(0.392699X) (21) 3 (22)
Y = A(C) + A(C+1)d + A(C+2)d2 + A(C+3)d 6
+ A(C+4)d4 + A(C+5)d5 + A(C+6)d The corresponding values for the A(C) , A(C+1) , A(C+2),
A(C+3), A(C+4) , A(C+3) and A(C+6) terms are as follows:
-3.17821 A(33) == 7.552876 A(1) = .82569984 A(2) = .153463 A(34)
.0759066 A(35) w .036134823 A(3) =
-53.7335 A(4) = 0. A(36) =
A(37) = 45.3671 A(5) = 0.
-15.3282 A(6) = 0. A(38) =
A(39) = 2.24735 A(7) = 0.
.122674 A(8) = -25.7 31 A(40) =
A(9) = 26.2'/38 A(41) = 0.
A(42) = 0.
A(10) = -11.3014 -674.351 A(11) = 2.04278 A(43) =
= .134412 A(44) == 384.531 A(12) -73.7766 A(13) = 0. A(45)
A(46) = 4.72041 A(14) = 0.
A(15) = -47.5827 A(47) = 0.
)
= 0.
A(16) == 43.8050 A(48)
A(49) = 0.
A(17) = -16.0781 2.53726 A(50) = -55.5622 A(18) = = 53.6534 A'19) .148044 A(51)
A(52) = -20.6300 A(20) = 0.
3.44177 A(21) = 0. A(53) =
A(54) = .212314 A(22) == -128.5278 A(23) 77.28943 A(55) = 0.
A(24) = ' 15.90284
- A(56) = 0.
1.071885 A(57) = 436.987302 A(25) -755.860224 A(26) = 0. A(58)
A(59) = 515.64145 A(27) = 0.
-181.713295 A(28) = 0. A(60) =
41.824767 A(61) = 35.153579 A(29) =
= -3.558356 A(30) n -103.969677 A(62)
= 86.215344 A(63) = .14774 A(31)
A(32) = -35.1021096 9-11 Rev.6-12/89 .
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9.2.10 Ground Level X/O. D2DPXO, D1XO. D/O Analvnis 9.2.10.1 EDdocaved. Undenleted Plume Relative Concentration, X/O The atmospheric concentration of offluent at ground level, normalized by the source term Q, is given by the following equation:
3 X/Q = 2.032(TCORR) , soc /m (23)
WSPL(X) Amin wher o Amin = The losser of the two values obtained by equations (24) and (25), motor _
A1= (a2g + Iz) , motor (24)
A2" (3) 0: , motor (2.5) 3.032 = The constant (2/w) b divided by the width in radians of a 22.5*
sector (i.e., w/8), dimensionless X = Distance between relcano point to receptor, meter
)
9.2.10.2 Decaved. Deoleted Radiciodino and Particulate Relative Concentration, D2DPXO The decayed, depleted radiciodine concentration, D2DPXQ, is calculated in accordance with the following equation:
3 D2DPXQ = DPP (DC2) X/Q , sec/m (26) where DPF = The depletion factor calculated per section 9.2.9, dimensionless DC2 = The radioiodine decay factor, dimensionless
= exp (-0.693(X)/tg (WSP L)]
= exp (-0.693(X)/(8 day)(24 hr/ day)
(3600 sec/hr) (WSPL )]
= exp (-1.00E-06 (X/WSP L))
)
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9.2.10.3 Decaved Noble Gac Plume Relative Concentration. D1XO The decayed noble gas plume relative concentration, D1XQ, is calculated in accordance with the following equations 3
D1XQ = DC1 (X/Q) , sec/m (27) :
where DC1 = The nobis gas decay factor,
- dimensic71ess
= exp (-0. 693 (X)/tg (WSPL) ] !
= orp (-0.693(X)/(2.26 day)(24 hr/ day)
(3600 sec/hr)(WSPL)3
= exp (-3.55E-06 (K/WSPL )]
9.2.10.4 Radiciodine and Particulate Relative Denosition. D/O The relative deposition for radiciodines and particulates, D/Q is calculated in accordance with the fo?. lowing equation:
D/Q = DPSF(DC2)(TCORR), m"2 (28)
(2w/16) X where .
DPSF = The deposition factor calculated per section 9.2.9, m' 9.2.11 Elevated X/O. D2DPXO. D1XO. D/O Analysis 9.2.11.1 Undecayed. Undeeleted Plume Relative Concentration. X/O The atmospheric concentration of effluent at ground level, normalized by_the source term Q, is given by the following equations X/Q = 2.032(1-TCORR)erp(-0.5(H/ag)2), sec/m 3 (29)
STACWS (X) az where=all parameters are as previously defined.
CLINTON-1 9-13 Rev.6-12/89 y ._ _ _ _ _ _ _.. _ . _ _ _ _ _ _ _ _ _ ___ ___
_ _ _ _ __._..=__._._m _ __ _ _ . _ .
CPS-ODCM 9.2.11.2 Decayed, Den 10ted Radiciodine and Particulate Relative Concentration, D2DPXO The calculation of D2DPXQ for elevated releases follows section 9.2.10.2 methodology with the exception that the WSPL value used in the calculation of DC2 in equation (26) is replaced by the STACWS value and the equation (29) X/Q is used. ,
9.2.11.3 Decayed Noble Gas Plume Relative Concentration. D1XQ The calculation of D1XQ for elevated releases follows j section 9.2.10.3 rathodology by substituting the equation (29) X/Q value into equation (27) and STACWS for WSPL in the calculation of DC1. ;
l 9.2.11.4 Rad'oiodine and Particulate Relative Deposition, D/O I The calculation of D/Q for elevated releases follows section 9.2.10.4 methodology by substituting (1-TCORR) for the TCORR term in equation (28) and STACWS for WSPL i in the calculation of DC2.
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b
{. .)
oCLINTON-1 9-14 Fev.6-12/89
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Table 9.2-1
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.GASEQUS EFFLUENT RELEASE POINT CHARACTERISTICS t
, t mAswastsno !
- tunsix
.oo, su.s.cas
- o. uv -
ACC# o.7817 i
nn ,
, un CCMTRot. AccW q
- sets vuur a muuma N tarts W cowtsmuner teue. EL. t t?v conTnes. sus.nas
- ,, .', . L noon a.s4rv QQ
~ ~ ~ ~ '
j ',
al dd ccamaserr [
l
_ _/
acco c nov w)_
g ; 4'\ /
p c' - g /
/ s .
- ua. m .
~ / - !.ee.u.nw m
~ ~
= ~ K =_~=.';9 y ,'
- E K =.','9 ?1i
, aussa.cas.us wec suussa y/ m s m sutuitoers car r .riev) t - - -.. - J HVAC Exhaust Stack SGTS Exhaust Stack
' Release. Point Height (m) 61 61 Building' Height- (m) 58 58 ,
Release Po. int-Geometry Duct Pipe -
Release-Point Araa-(m2).
11.15 0.15 -
-Release-Point Diameter (m) 3.77* 0.44 Annual Average Flow Rate (m 3/sec) d1.71 1.89 1:
l ' Vertical Exit VeJocity (m/sec) 10.02 12.49
'*Ef fective 2 ( A/r) b diameter )!
CLINTON-1_ 9-15 Rev.6-12/89 <
s ,. , , , - _ . - . . . , . . . -,-.-_. ---+ - . .----- . -.. .. ._.- - -._ . _ - - - - - - - . . - - - - - -_ _ _ _
BLLBMOBS POUJM
- m
_--- -- _ _ _ _ _ -.- - _ _ - -m __.-__- --_-_.m_-- - - - . - _ _m__-._ __-- -. .