U-602989, Annual Radioactive Effluent Release Rept for Clinton Power Station,Jan-Dec 1997
| ML20217K314 | |
| Person / Time | |
|---|---|
| Site: | Clinton  |
| Issue date: | 12/31/1997 |
| From: | Sipek J ILLINOIS POWER CO. |
| To: | NRC OFFICE OF INFORMATION RESOURCES MANAGEMENT (IRM) |
| References | |
| U-602989, NUDOCS 9805010156 | |
| Download: ML20217K314 (517) | |
Text
{{#Wiki_filter:% llisnois Power Company
. Chnton Power Station e- P.O Box 678 Cisnton,IL 61727 Tel 217 935-8881 Joseph V. Sipek g Director - Licensing An ano . comp.ny U-602989 1A.120 March 24, 1998 Docket No. 50-461 10CFR50.36a 10CFR50, App I, IV.B.1 Document Control Desk Nuclear Regulatory Commission Washington, D.C. 20555
Subject:
Clinton Power Station Annual Radioactive Efiluent Release Report
Dear Madam or Sir:
Attached is the Annual Radioactive EfYluent Release Report for Clinton Power Station (CPS) for the period of January 1,1997 through December 31,1997. This submittal is provided in accordance with the requirements of section 5.6.3 of the CPS Technical Specifications. Sincerely yours, os h V. Efi et irector - Licensing GBS/mlh Attachment cc: NRC Clinton Licensing Project Manager NRC Resident Office, V-690 \ Regional Administrator, Region III, UShRC Illinois Department ofNuclear Safety
- A/
Eg 9905010156 971231 PDR ADOCK 05000461 R PDR
ANNUAL RADIOACTIVE EFFLUENT RELEASE REPORT FOR THE CLINTON POWER STATION 1 January 1,1997 - December 31,1997 Prepared by l Plant Radiation Protection and Chemistry Department i l l l April 24,1998 l l
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i l i January 1,1997 - December 31,1997 ANNUAL RADIOACTIVE EFFLUENT RELEASE REPORT FOR THE CLINTON POWER STATION Prepared by Plant Radiation Protection and Chemistry Department l I April 24,1998 i i l J
TAIILE OF CONTENTS SECTION 1%Q3
- 1. Executive Summary . . . . . .. ... . ... .. . . .5 l
1 Introduction. .
- 2. . . ..... . . . . . .. .... . ....... .. .6
- 3. Supplemental Information. .. . .. . . . . . 13 i
- 4. Effluent and Waste l)isposal Data. . . ... . . . . .18
- 5. Meteorological Data and Dispersion Estimates. .. ..... .. . .. . .. . . 29
- 6. Dose Measurements and Assessments . . . .. ..... . .. . .. 40
- 7. Changes to the Offsite Dose Calculation Manual. . . . . . . . . . . . . . . . . . . ..... .50
- 8. ODCM Operational Requirement Reports. . . . . . . . . . . . . . . . ........ .. .51 1
- 9. Major Changes to Radioactive Waste Treatment Systems . . . . . . . . . . . . . . . . .. . . . . 55
- 10. New Locations for Dose Calculation and/or Environmental Monitoring. . . . . . . . . . . 56
- 11. Corrections to Data Reported in Previous Reports . ........... ..... . . . . . 59 2
l 1 I l LIST OF TAllLES i 1 I PAGE Table 1: Airborne Effluents . Summation of All Releases . . . . . . . . . ... .... 18 Table 2: Airborne Effluents . . . . . .. ........... .. ... ...., . ..... 19 l Table 3: Itadioactive Gaseous Waste LLD Values . . ... ..... .. . .... . 20 Table 4: Waterborne Effluents - Summation of All Releases . . . . . . . . . . . . . . . . 22 Table 5: Waterborne Effluents . . .. ... ..................... ...... 23 Table 6: Radioactive Liquid Waste LLD Values. . . . . . . . . . . . . . . . . . . ...... 24 l Table 7: Solid Waste and Irradiated Fuel Shipments. . . . . . . . . . . . . . . . . . . . . . 27 i Table 8: Meteorological Data Availability . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 30 Table 9: Classification of Atmospheric Stability. . . . . . . . . . . . . . . . . . . . . . . . . . . 31 l Table 10: Joint Wind Frequency Distribution by Stability Class. . . . . . . . . . . . .. . 32 Table 11: Maximum Offsite Doses and Dose Commitments l to Members of the Public . . . . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . .. 4 0 ! Table 12: Calculated Doses to Memters of the Public
- During Use of the Department of Natural Resources l Recreation Area in the East. Southeast Sector l within the CPS Site Boundary . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .43
( Table 13 Calculated Doses to Members of the Public During Use of the Road in the Southeast Sector within the CPS Site Boundary. . . . . . . . . . . . . . ..................44 Table 14: Calculated Doses for the Residents in the South. Southeast - Sector within the CPS Site Boundary . . . . . . . . . . . . . . . . . . . . . . ... 45 Table 15: Calculated Doses for the Residents in the Southwest Sector within the CPS Site Boundary . . . .. . . . . . . . . . . . . . . . . . . . . . . . . . 46 i 3
- LIST OF TABLES (continued)
PAGE Table 16: Calculated Doses to Members of the Public During Use cf the Agricultural Acreage in the South-Southwest Sector within the CPS Site Boundary. . ... 47 Table 17: Calculated Doses for the Residents in the West. Southwest Sector within the CPS Site Boundary . .. .. 48 Table 18: Calculated Doses to Members of the Public During Use of Clinton Lake in the Northwest Sector within the CPS Site Boundary. . ... ................... ......49 LIST OF FIGURES PAGE l Figure 1: CPS Airborne Effluent Release Points . . . . . . . . . . . . . . . . . . . . . . . . . . . 7 Figure 2: CPS Waterborne Effluents Release Pathway . . . . . . . . . .... ..... .8 Figure 3: Effluent Exposure Pathways . ...... .... . ...... . . 12 Figure 4: Areas Within the CPS Site Boundary Open to Members of the Public . . . . . . . ............... . . . . ......... 42 4
SECTION 1 EXECUTIVE SUMMAltY The Annual Itadioactive Effluent Itelease Report is a detailed description of all radioactive releases (both gaseous and liquid) from the Clinton Power Station (CPS) and the resulting radiation doses for the period from January 1,1997 through December 31, 1997. This report includes a detailed meteorological section which provides the 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 cddition, this report notifies the U.S. Nuclear Regulatory Commission (NRC) staff of changes to CPS's Offsite Dose Calculation Manual (ODCM) and exceptions to the CPS cffluent 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 effluent 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 of radioactivity in effluents. 1 CPS was operated in compliance with established limits during this report period. The maximum i radiation dose delivered to the inhabitants of the area surrounding CPS, due to radioactivity l released from the station, was very small. The radiation dose to people in the vicinity of CPS was l calculated for a continuous gaseous release by using the concentration of radioactive material and l the weather conditions at the time of the release. This dose was only a small fraction of the limit for the most exposed member of the public and came entirely from gaseous releases from the site. There were no liquid releases in 1997. l 1 1 I i i l 5
SECTION 2 INTRODUCTION Clinton Power Station is located in Ilarp Township, DeWitt County approximately six miles east of the city of Clinton in east-central lilinois. 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 I3aldwin 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 released from CPS via two ganyus effluent release points to the environment: the Common Station Heating, Ventilating, and Air Conditioning (HVAC) Stack and the Stondby 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. Liquid effluents from CPS are released in batch mode and are sampled and 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 seal well prior to entering the 3.4 mile discharge fiume to Lake Clinton (see Figure 2). 6
i Figure 1 CPS AIRBORNE EFFLUENT RELEASE POINTS m.m.ou o Ru-u uo / ROOF Q. 876'0* MACHDE QCP BUILDDC ROOF Q 781'0* 170'0* l j 2067 CONTROL ROOM - t AIR HANDUNC k'GTS VDff MS Top coMTAINMD(T CONC,H.92TO'
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--- G - _ Y IWAC Exhaust SGTS Exhaust Stack Stack Release Point Height (m) 61 61 Building Height (m) 58 58 Release Point Geometry Duct Pipe Release Point Area (m') 11.15 0.15 Release Point Diameter (m) 3.77* 0.44 Annual Average Flow Rate (m*/sec) 111.71 1.89 Vertical Exit Velocity (m/sec) 10.02 12.49 7
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Figure 2. CPS WATERBORNE EFFLUENTS RELEASE PATHWAY - J l
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RE (AT LEAST S000 GPM)
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LIQUID RADWASTE DISCHARGE LINE . (10-60 OR 60-300 GPM) h . RADIATION MONITOR ALNW/TRP SEIPOURCM4ULATED BASED - ON EAOiBMCHISOTOPIC ANMYSIS /ND otumON RDW M ISOLATION VALVE TERMINATES RELEASE ON I4GH RADIA110N. ISGH RELEASE RDW RATE.OR Low OtLUTION ROW RAE
@ COMPOSITE SAMPLER courcTsweRoMMMELY20 mt EVERY60laARES fWjN THE DISCHARGE FUME FOR SAORINLY ANALYSIS SEALWELL O LAKE P L ANT CIRCULATING :
WATER CLINTON (0-567.000 GPM) DISCHARGE FLUME 3A 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 Offsite Dose Calculation Manual (ODCM) governing the release of radioactive effluents (Code of Federal Regulations, Title 10, Part 50, Appendix I). The ODCM designates 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. L l
-and-
- Less than or equal to 10 mrem per year to any organ. )
I The dose to a member of the general public from the 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. 1 These ALARA limits are a fraction of the dose limits established by the Environmental Protection Agency (EPA). In its Environmental Dose Standard of 40CFR190, the EPA established dose limits for members of the public in the vicinity of a nuclear power plant. These dose limits are:
- Less than or equal to 25 mrem per year to the total body.
- Less than or equal to 75 mrem 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. O
Processine and Monitorine Effluents are strictly controlled at CPS to ensure radioactivity released to the environment is l minimal and does not exceed release limits. Effluent controls include the operation of radiation !
- monitoring systems in the plant and offsite environmental sampling and analysis programs. In.
l 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 analyzed in a , laboratory to identify the specific concentration of radionuclides being released. Sampling and j analysis provide a more sensitive and precise method of determining effluent composition to . ( complement the information provided by real-time monitoring instruments. I l Heyond 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 on the environment due to the operation of the Clinton Power Station. l 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 l program consists of two phases, pre-operational and operational. During the pre-operational l phase of the program, the baseline for the local radiation environment was established. The operational phase of the program includes the objective of making confirmatory measurements to l verify that the in-plant controls for the release of radioactive material are functioning as designed. l Assessment of the operational impact of CPS on the environment is based on data collected since l initial reactor criticality. l Exposure Pathways l , Radiological exposure pathways are the means by which people may become exposed to L radioactivity released from nuclear facilities. The major pathways of concern are those which l could cause the ? ghest calculated radiation dose. These pathways are determined from the type l 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 by wind speed and wind direction at the time of the release. This information is used to evaluate how the radionuclides will be distributed in the l area. The most important factor in evaluating the exposure pathway is the use of the l 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 very l important considerations in evaluating exposure pathways. Figure 3 illustrates the various 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 fish consumption and direct exposure from the lake. Dose Assessment Whole body radiation involves the exposure of all organs in the human body to ionizing radiation. Most background radiation exposures consist of whole body exposure although specific organs can receive radiation exposure from distinct radionuclides. These radionuclides enter the body through inhalation and ingestion and seek different organs depending on the nuclide. For. example, radioactive iodine selectively concentrates in the thyroid, radioactive cesium collects in muscle and liver tissue, and radioactive strontium in mineralized bone. 10
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 in all sixteen geographical sectors surrounding CPS and takes into account the location of the nearest residents, vegetable gardens producing broad leaf vegetables, dairy and meat animals in all sectora. The calculated dose also 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 11-18 of Section 6 for more detailed information on dose to the public. Gaseous Psffluents Gaseous effluent radioactivity released from CPS is classified into two categories,1) noble gtses, and 2 ) 8881, 1881, aH and all radionuclides in particulate form with halflives greater than eight days. Noble gases, such as xenon and krypton, are biologically and chemically nonreactive; these radionuclides cause external radiation exposure. *8*I,188I, 8H and radionuclides in particulate form with half-lives greater than eight days are the major contributors to internal dose. See Tables 1,2, and 3 of Section 4 for more detailed information on gaseous effluents. Liould Effluents CPS had no radioactive liquid discharges in 1997. 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 CPS is complying with these regulations, the types of waste and the radioactivity present are reported to the NRC. See Table 7 of Section 4 for more detailed information on solid waste shipments. ll i j
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SECTION 3 SUPPLEMENTAL INFORMATION 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 II, Table 2, 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. 1831,28I,8H 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 Title 10 of the Code of Federal Regulations, Part 50, Appendix I, air dose due to noble gases released in gaseous effluents to areas at and beyond the site boundary shall be limited to the following:
- a. Less than or equal to 5 mrad for gamma radiation and less than or equal to 10 mrad for beta radiation during any calendar quarter.
- b. Less than or equal to 10 mrad for gamma radiation and less than or equal to 20 mrad for beta radiation during any calendar year.
- 3. In accordance with 10CFR50, Appendix I, dose to a member of the public (from 5881, 188I,811 and all radionuclides in particulate form with half lives greater than eight days) in 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 organ, during any calendar year.
13
I). Liquid Effluents
- 1. The concentration of radioactive material released in liquid effluents to unrestricted areas shall be limited to the concentrations specified in Title 10 of the Code of Federal Regulations, Part 20, Appendix B, Table 2, Column 2, for radionuclides other than dissolved or entrained noble gases. For dissolved or entrained noble gases, the concentration shall be limited to 2.0E-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 than 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. AVERAGE ENERGY The CPS ODCM limits the dose equivalent rates due to the release of fission and activation gases to less than or equal to 500 mrem per year to the total body and less than or equal to 3000 mrem per year to the skin. These limits are based on dose calculations using actual isotopic concentrations in our effluent streams, and are not based upon gross count monitors. Therefore, the average beta and gamma energies (E) for gaseous effluents 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", are not applicable. III. MEASUREMENT AND APPROXIMATIOK OF TOTAL RADIOACTIVITY A. Fission and Activation Gases
- 1. Gas samples are collected weekly and are counted on a high purity germanium detector (HPGe) 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. Tritium is collected 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 q volume of the sample, the tritium collection efficiency, and the stack exhaust flow '
rates. 14
Il lodines Iodine is continuously collected on a charcoal cartridge 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 these results, along with isotopic concentrations, are used 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 on 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. D. Liquid Effluents Each tank ofliquid radwaste is sampled and analyzed for principal gamma emitters prior to release. Each sample tank is recirculated for a sufficient amount of time prior to sampling to ensure that a representative sample is obtained/ Sam"ples are analyzed on an HPGe system and release permits are generateil based on the vclues obtained from the isotopic analysis and the most recent values for 3H, gross alpha, "Fe,89Sr and "Sr. 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. 15
l' . IV. IIATCH RELEASES A. Liquid 1997
- 1. Number of bakh' releases: 0
- 2. Total time l_ period for l batch releases: N/A l 3. Maximum time period for batch release: N/A
- 4. Average time l
period for batch release: N/A
- 5. Minimum time period for.
batch release: N/A
- 6. Average stream I flow during periods of release: N/A
- 7. Total waste volume: N/A
- 8. Total dilution volume: N/A l
B. Gaseous 1997
- 1. Number of batch releases: 0
- 2. Total time period for batch releases: N/A
- 3. Maximum time period for batch release: N/A
- 4. - Average time period for batch release: N/A
- 5. Minimum time period for batch release: N/A .
4 16 s .
V. AllNOllMAL llELEASES CPS had no abnormal release of radioactive liquid during 1997. A. Liquid 1997
- 1. Number of abnormal l
releases: 0
- 2. Total time period for I abnormal releases: N/A
- 3. Maximum time period for abnormal release: N/A
- 4. Average time period for ,
abnormal release: N/A
- 5. Minimum time period for abnormal release: N/A
- 6. Average stream flow during periods of release: N/A
- 7. Total waste volume: N/A
- 8. Total dilution volume: N/A l
VI. DESCRIPTION OF ERROR ESTIMATES l A. Gaseous and Liquid Effluents Estimates of measurement and analytical error for gaseous and liquid effluents are calculated as follows: E T= [(E,)2 + (E2 ) + ...(E n ) where, E7 = total percent error E,,,,E,= percent error due to calibration standards, laboratory analysis, instruments, sample flow, etc. 17 - i
SECTION 4 - EFFLUENT AND WASTE DISPOSAL DATA TABLE 1 AIRBORNE EFFLUENTS - SUMMATION OF ALL RELEASES Data Period: January 1,1997 - December 31,1997 Continuous Mode Est. Totali Nuclide Cateeory Unit Error. % A. Fission & Activation Gases
- 1. Total Release Ci 0.00E+00 30
- 2. Average Release Rate for Period Ci/sec 0.00E+00
- 3. Percent of .
Applicable Limit % 0.00E+00 . B. Iodine-131
- 1. Total Release Ci 0.00E+00 31
- 2. Average Release Rate for Period Ci/sec 0.00E+00 C. Particulates
- 1. Particulates Released released with Half lives > 8 Days Ci 6.77E-05 24
- 2. Average Release Rate for Period pCi/see 2.15E-06
- 3. Gross Alpha Activity Released Ci 2.54 E-06
- 4. Gross Alpha Average Release Rate for Period Ci/sec 8.06E-08
- 5. Percent of Applicable Limit for Particulates, and Iodine % 4.83E-02 D. Tritium
- 1. Total Release Ci 3.41E+00 105
- 2. Average Release Rate for Period pCi/see 1.08E 01
- 3. Percent of Applicable % 4.16E-03 Limit -
8 It should be noted that the lower the actual sample activity is with respect to background l activity, the greater the counting error. Large errors are reported for the various components of CPS gaseous effluents because of consistently low sample activity. f 18 t
TAlli,E 2 AlltHORNE EFFLUENTS (Curies)' Data Period: January 1,1997 - December 31,1997 Continuous Mode Nuclide Value (Ci) A. Gases None Released 0.00E+00 Total 0.00E+00 B. Iodines None Released 0.00E+00 j Total 0.00E+00 ! C. Particulates w/ Half-lives > 8 Days 54Mn 8.21 E-06 80Co 3.74E-05 89Sr 4.61 E-06 Total 5.02E-05 2 Absence of a nuclide from the above list does not indicate that it was not present. It simply indicates that it's Minimum Detectable Activity (MDA) was below its LLD. See Table 3 for a list of the LLDs of the various nuclides. 19 s
TAllLE 3 RADIOACTIVE GASEOUS WASTE LLD VALUES Lower Limit of TYPE OF Detection (LLD)= ACTIVITY ANALYSIS (uCi/mD b Principal Gamma Emitters # 1x10 04 311* 1x10 06 d isiI 1x10-12 d isaI 1x10-10 Principal Gamma Emitters'# 1x10-II (281I, others) Gross Alpha' 1x10-Il 88Sr, "Sr' 1x10-Il Table 3 Notations "The LLD is defined, for purposes of these specifications, as an "a priori" determination of 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 and with only 5% probability of falsely concluding that n blank observation represents a "real" signal. For a particular measurement system, which may include radiochemical separation:
"# 6 LLD =
E V 2.22 x 10 6 Y e "^' 20
1 Table 3 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 blank sample as appropriate, as counts per minute, E is the counting efficiency, as munts per disintegration, V is the sample size in units of mac 1 w N me. 2.22 x 106 is the number of disintegrations per minute per microcurie, Y is the fractional radiochemical yield, when applicable, A is the radioactive decay constant for the particular radionuclide (sec 1) and At for plant effluents is the elapsed time between the midpoint of sample col.lection 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 particular measurement.
'The principal gamma emitters for which the LLD specification applies include the following radionuclides: 87Kr, 88Kr, 288Xe, ia3=Xe,185Xe, and 288Xe in noble gas releases and 54Mn, 59Fe, 58Co, "Co,65Zn,89Mo,1821, 284Cs,187Cs,143Ce and "Ce 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 Radioactive Effluent Release Report. ' Weekly grab sample and analysis
' Continuous charcoal sample analyzed weekly- ' Continuous particulate sample analyzed weekly ' Composite particulate sample analyzed monthly 8 Composite particulate sample analyzed quarterly 21
TAllLE 4 WATERIlORNE EFFLUENTS - SUMMATION OF ALL RELEASES Data Period: January 1,1997 - December 31,1997 Est. Total Nuclide Category Unit Value Error. % A. Fission & Activation Products
- 1. Total Release Ci 0.00E+00 N/A
- 2. Average Diluted Concentration pCi/ml 0.00E+00
- 3. Percent of Applicable Limit % 0.00E+00 B. Tritium
- 1. Total Releases Ci 0.00E+00 N/A
- 2. Average Diluted Concentration pCi/ml 0.00E+00
- 3. Percent of Applicable Limit % 0.00E+00 C. Dissolved and Entrained Gases
- 1. Total Releaset Ci 0.00E+00 N/A
- 2. Average Diluted Concentration Ci/ml 0.00E+00
- 3. Percent of Applicable Limit % 0.00E+00 D. Gross Alpha Radioactivity Released 2 Ci 0.00E+00 N/A E. Volume of Waste Released gallons 0.00E+00 N/A liters 0.00E+00 F. Volume of Dilution gallons 0.00E+00 N/A Water Used liters 0.00E+00 Notation: 1 An entry of 0.00E+00 does not represent the absence of a radionuclide but i
indicates that the MDA concentration of the nuclide was below the LLD value listed in Table 6. 2 A sample was not analyzed for these activities. 6 22
TAllLE 5 WATEltllOltNE EFFLUENTS (Curies) Data Period: January 1,1997 - December 31,1997 All Modes Nuclide Category Activity A. Tritium N/A B. Fission & Activation Products 53Cr N/A 54Mn N/A 58Co N/A "Co N/A 55Fe N/A HFe N/A "Zn N/A 89Sr N/A "Sr N/A N/A 98Mo 124Sb N/A 281I N/A 283I N/A l 184Cs N/A 287Cs N/A 340Ba N/A 2*La N/A 243Ce N/A 120 mag N/A Total N/A C. Dissolved and Entrained Gases 85Kr N/A 85=Kr N/A 87Kr N/A 88Kr N/A 888Xe N/A 288mXe N/A 285Xe N/A 885=Xe N/A 188Xe N/A Total N/A 23
TAllLE 6 ItADIOACTIVE LIQUID WASTE LLD VALUES LOWER LIMIT OF DETECTION (LLD)" TYPE OF ACTIVITY ANALYSIS (uCi/ml) Principal Gamma Emitters' 5x10-7 isil 1x10-6 Dissolved and Entrained Gases (Gamma Emitters) 1x10-5 aH 1x10-5 Gross Alpha 1x10-7 l 8987, MSr 5x10-8 HFe 1x10-6 Table 6 Notations "The 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 and only 5% probability of falsely concluding that a blank observation represents a "real" signal. For a particular measurement system, which may include radiochemical separation:
'# 6 LLD =
E V 2.22 x 10 6 Y e - '^' l 24
l I Table 6 Notations (Cont'd) Where: 1 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 sampic size in units of mass or volume,
)
2.22 x 106 is the number of disintegrations per minute per microcurie, l Y is the fractional radiochemical yield, when applicable, A is the radioactive decay constant for the particular radionuclide (sec-1) and At for plant effluents is the elapsed time between the midpoint of sample collection ; and the time of counting (sec). i 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, MDA) limit for a particular measurement. The principal gamma emitters for which the LLD requirement applies ~ include the following ; radionuclides: 64Mn, "Fe, 68Co, "Co, "Zn, "Mo, 384Cs,187Cs, and H Ce. H4Ce shall also be ' measured, but with an LLD of 5 x 10 6. This list does not mean that only these nuclides are to be d:tected and reported. Other gamma peaks that are measurable, together with those of the above nuclides, shall also be analyzed and reported in the Radioactive Effluent Release Report. 25
1 SOLID WASTE AND IRRADIATED FUEL SHIPMENTS During this reporting period there were nineteen (19) radioactive waste shipments and no l irradiated fuel shipments from CPS as reported in Table 7. In addition, the CPS ODCM requires reporting of the following information for solid waste shipped offsite during the report period: Class A:
- 1. Container volume: 208.4 ft',195.2 ft*,195.7 ft*,135.8 ft*, 73.4 ft*,669 ft *.
- 2. Total curie quantity: 962 curies as determined by dose to-curie and sample concentration methodology estimates.
- 3. Principal radionuclides: See Table 7, A.2 for listing of measured radionuclides.
- 4. Source of waste and processing employed: Resins, filter sludges nnd evaporator bottoms dewatered or solidified in cement, and non-compacted dry active waste.
- 5. Type of container: Type A and Strong Tight Container.
- 6. Solidification agent or absorbent: None.
These containers were shipped to a waste processor, not a burial site. t l l l 26
TABLE 7 SOLID WASTE AND IRRADIATED FUEL SIIIPMENTS January 1,1997 - December 31,1997 A. SOLID WASTE SHIPPED OFFSITE FOR BURIAL OR DISPOSA.L (not irradiated fuel) EST. TOTAL
- 1. TYPE OF WASTE UNIT VALUE ERROR,%
- a. Resins, filter sludges, m' 7.85E+01 evaporator bottoms, Ci 9.62E+02 25 etc.
- b. Dry compactible m' 2.65E+02' waste, contaminated Ci 3.70E-01 25 equipment, etc.
- c. Irradiated components, m 0.00E+00 control rods, etc. Ci 0.00E+00 0
- d. Other m' O.00E+00 Ci 0.00E+00 0
- 2. LSTIMATE OF MAJOR NUCLIDE COMPOSITION NUCLIDE PERCENT NAME ABUNDANCE CURIES
- a. Co 60 21.00% 2.02E+02 Mn 54 8.65% 8.32E+01 Fe-55 63.84 % 6.14 E+02 OTHER 6.51% 6.26E+01
- b. Fe-55 84.65 % 3.14 E-01 Co-60 10.05% 3.73E-02 Mn-54 4.62% 1.71E-02 OTHER 0.68% 2.52E-03
- c. NONE N/A N/A
- d. NONE N/A N/A 2
Actual volume reduc 9d by waste processor. e 27
TABLE 7 (Cont'd) SOLID WASTE AND IRRADIATED FUEL SHIPMENTS January 1,1597 - December 31,1997
- 3. SOLID WASTE DISPOSITION NUMBER OF MODEOF SHIPMENTS TRANSPORTATION DESTINATION 15 Truck Barnwell, SC 4 Truck Oak Ridge, TN B. IRRADIATED FUEL SHIPMENTS (Disposition)
NUMBER OF MODE OF SHIPMENTS TRANSPORTATION DESTINATION NONE N/A N/A 28 L . .. .
SECTION 5 METEOROLOGICAL DATA AND DISPERSION ESTIMATES l The meteoroiogical monitoring program began at the Clinton Power Station site on April 13,1972. 1 The meteorological system consists of a tower 199 feet high with two levels ofinstrumentation, at j the 10-meter and 60 meter levels. Wind directions and speeds at the 10-meter and 60 meter j levels are measured by a combined cup and vane sensor. The temperature at these levels is ! scnsed by an aspirated dual temperature sensor. One-half of the dual sensor at each elevation is used for ambient temperature while the other 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 dew-point sensor. l 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 received and converted to a 4 to 20 milliamp signal end fed individually 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 and the Technical Support Center. 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 paints. 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 assigned the previous hour's wind direction. Periods of calm are assigned a wind speed value of half the specified instrument threshold value. See Table 10 for more detailed information on meteorology and dispersion data.
)
l I i l 29 1
TABLE 8 METEOROLOGICAL DATA AVAILABILITY Data Period: January 1,1997 December 31,1997 Percent of Valid Parameter Hours Durine Period (1)
- 1. Wind Speed a.10 meter Sensor 94%
- b. 60 meter Sensor ,
94 %
- 2. Wind Direction a.10-meter Sensor 94%
- b. 60 meter Sensor 94%
- 3. Temperature -
a.10-meter 94 %
- b. 60 Meter 94%
- b. Temperature Difference (10m-60m) 94 %
- 4. Percent of hours for which valid 94%
10-meter Wind Speed, Wind Direction,
& Delta Temperature were available
- 5. Percent of hours for which valid 94%
60-meter Wind Speed, Wind Direction,
& Delta Temperature were available j (1) There was no invalid data for 1997. The values reported here represent the hours that data was not missed.
30 1
TAHIE 9 CLASSIFICATION OF ATMOSPHERIC STABILI'lY Stability Classification- Pasquill Category Defining Conditions Extremely unstable A -0.900<ATS-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 stable E -0.005<aTs 0.015 Moderately stable F 0.015<ATs 0.040 Extremely stable G 0.040<ATS 0.900 Invalid ATs-0.900 or AT>0.900 AT = temperature difference in Celsius degrees per meter I 4 e 31
.j
TAllLE 10. Pace 1 of 8 JOINT WIND FREQUENCY DISTRIBUTION HY STABILITY CLASS For the Period January 1,1997 - December 31,1997
' STABILITY CLASS A 60 Meter (All tabled values are Hours)
SECTOR 1-3 mph 4-7 mph 8-12 mph 1318 mph 19-24 mph >24 mph TOTAL N 0.00E+00 9.00E+00 4.80E+01 1.80E+01 0.00E+00 0.00E+00 7.50E+01 NNE 1.00E+00 6.00E+00 2.00E+01 3.00E+01 8.00Eu ^00E+00 6.50E+01 NE 2.00E+00 1.90E+01 1.40E+01 1.50E+01 7.00E+0L 30E+00 6.00E+01 ENE 1.00E+00 2.40E+01 2.10E+01 1.70E+01 4.00E+00 3.00E+00 7.00E+01 E 7.00E+00 2.20E+01 3.50E+01 9.00E+00 1.00E+00 1.00E+00 7.50E+01 ESE 7.00E+00 1.60E+01 2.00E+00 0.00E+00 0.00E+00 1.00E+00 2.60E+01 SE 1.70E+01 2.60E+01 1.30E+01 5.00E+00 0.00E+00 3.00E+00 6.40E+01 SSE 6.00E+00 2.30E+01 2.70E+01 7.00E+00 2.00E+00 3.00E+00 6.80E+01 S 7.00E+00 3.60E+01 4.70E+01 2.60E+01 1.20E+01 3.00E+00 1.31E+02 SSW 5.00E+00 5.30E+01 4.60E+01 3.90E+01 1.10E+01 1.00E+00 1.55E+02 SW 2.00E+00 2.10E+01 3.20E+01 3.30E+01 1.00E+01 3.00E+00 1.01E+02 WSW 5.00E+00 2.60E+01 2.90E+01 1.30E+01 2.00E+00 9.00E+00 8.40E+01 W 1.00E+00 1.00E+01 2.10E+01 2.30E+01 2.10E+01 3.00E+00 7.90E+01 WNW 1.00E-02 1.20E+01 2.10E+01 3.70E+01 1.90E+01 7.00E+00 9.60E+01 NW 1.00E+00 1.70E+01 2.50E+01 4.00E+01 9.00E+00 7.00E+00 9.90E+01 NNW 0.00E+00 1.10E+01 2.50E+01 2.80E+01 1.00E+00 0.00E+00 6.50E+01 Total 6.20E+01 3.31E+02 4.26E+02 3.40E+02 1.07E+02 4.70E+01 1.31E+03 Periods of Calm (Hours): 1.00E+00 Hours of Invalid Data: 0.00E+00 10 Meter (All tabled values are Hours) SECTOR 1-3 mph 4-7 mph 8-12 mph 13-18 mph 19-24 mph >24 mph TOTAL N 3.00E+00 1.80E+01 5.80E+01 9.00E+00 0.00E+00 0.00E+00 8.80E+01 NNE 2.00E+00 1.80E+01 3.30E+01 8.00E+00 0.00E+00 0.00E+00 6.10E+01 NE 4.00E+00 3.10E+01 2.10E+01 1.20E+01 0.00E+00 0.00E+00 6.80E+01 ENE 4.00E+00 1.60E+01 8.00E+00 0.00E+00 0.00E+00 0.00E+00 2.80E+01 E 1.40E+01 4.50E+01 1.30E+01 0.00E+00 0.00E+00 0.00E+00 7.20E+01 ESE 8.00E+00 4.40E+01 6.00E+00 0.00E+00 0.00E+00 0.00E+00 5.80E+01 SE 1.10E+01 4.90E+01 2.50E+01 2.00E+00 0.00E+00 0.00E+00 8.70E+01 l SSE 9.00E+00 8.00E+01 4.10E+01 G.00E+00 1.00E+00 0.00E+00 1.39E+02 l S 8.00E+00 3.90E+01 4.80E+01 1.10E+01 2.00E+00 0.00E+00 1.08E+02 SSW 4.00E+00 2.60E+01 5.80E+01 1.80E+01 2.00E+00 0.00E+00 1.08E+02 SW 1.00E+00 1.80E+01 4.10E+01 2.00E+01 1.00E+00 1.00E+00 8.20E+01 WSW 3.00E+00 2.30E+01 2.30E+01 7.00E+00 1.00E+00 5.00E+00 6.20E+01 W 4.00E+00 2.20E+01 3.10E+01 3.10E+01 5.00E+00 2.00E+00 9.50E+01 WNW 1.00E+00 1.20E+01 3.90E+01 3.10F,+01 1.90E+01 0.00E+00 1.02 E+02 NW 2.00E+00 2.20E+01 3.40E+01 2.10E+01 1.00E+00 0.00E+00 8.00E+01 NNW 1.00E+00 1.10E+01 4.20E+01 1.80E+01 0.00E+00 0.00E+00 7.20E+01 Total 7.00E+01 4.74 E+02 5.21E+02 1.96E+02 3.20E+01 8.00E+00 1.31 E+03 Periods of Calm (Hours): 4.00E+00 Hours ofInvalid Data: 0.00E+00 32 (
TAllLE 10. Pane 2 of 8 JOINT WIND FREQUENCY DISTRIllUTION IlY STABILITY CLASS Data Period: January 1,1997 - December 31,1997 STABILITY CLASS 11 60 METER (All tabled values are Hours) SECTOR 13 mph 4 7 mph 8-12 mph 1318 mph l 19 24 mph >24 mph TOTAL N 1.00E+00 2.00E+00 1.90E+01 7.00E+00 0.00E+00 0.00E+00 2.90E+ 01 NNE 0.00E+00 4.00E+00 7.00E+00 3.00E+00 3.00E+00 0.00E+00 1.70Fs+01 NE 0.00E+00 5.00E+00 1.00E+00 4.00E+00 0.00E+00 0.00E+00 1.00E+01 ENE 4.00 E+00 1.00E+00 5.00E+00 2.00E+00 1.00E+00 0.00E+00 1.30E+01 E 2.00E+00 3.00E+00 4.00E+00 3.00E+00 2.00E+00 0.00E+00 1.40E+01 ESE 2.00E+00 4.00E+00 0.00E+00 1.00E+00 0.00E+00 0.00E+00 7.00E+00 SE 5.00E+ 00 3.00E+00 4.00E+00 0.00E+00 0.00E+00 0.00E+00 1.20E+01 SSE 2.00E+00 3.00E+00 2.00E+00 0.00E+00 1.00E+00 0.00E+00 8.00E+00 S 6.00E+00 5.00E+00 6.00E+00 4.00E+00 3.00E+00 1.00E+00 2.50E+01 SSW 2.00E+00 2.00E+00 7.00E+00 9.00E+00 5.00E+00 3.00E+00 2.80E+01 SW 1.00E+00 4.00E+00 1.00E+01 9.00E+00 2.00E+00 1.00E+00 2.70E+01 WSW 2.00E+00 2.00E+00 9.00E+00 4.00E+00 4.00E+00 3.00E+00 2.40E+01 W 2.00E+00 7.00E+00 6.00E+00 9.00E+00 5.00E+00 2.00E+00 3.10E+01 WNW 2.00E+00 5.00E+00 9.00E+00 9.00E+00 5.00E+00 4.00E+00 3.40E+01 NW 0.00E+00 7.00E+00 1.20E+01 8.00E+00 4.00E+00 1.00E+00 3.20E+01 NNW 0.00E+00 7.00E+00 9.00E+00 8.00E+00 2.00E+00 0.00E+00 2.60E+01 Total 3.10E+01 6.40E+01 1.10E+02 8.00E+01 3.70E+01 1.50E+01 3.37E+02 Periods of Calm (Hours): 0.00E+00 Hours of Invalid Data: 0.00E+00 10 METER (All tabled values are Hours) SECTOR 1-3 mph 4-7 mph 8-12 mph 1318 mph 19-24 mph >24 mph TOTAL N 2.00E+00 3.00E+00 2.20E+01 6.00E+00 0.00E+00 0.00E+00 3.30E+01 NNE 1.00E+00 8.00E+00 7.00E+00 0.00E+00 0.00E+00 0.00E+00 1.60E+01 NE 9.00E+00 4.00E+00 3.00E+00 0.00E+00 0.00E+00 0.00E+00 7.00E+00 ENE 4.00E+00 7.00E+00 1.00E+00 0.00E+00 0.00E+00 0.00E+00 1.20E+01 E- 3.00E+00 5.00E+00 4.00E+00 0.00E+00 0.00E+00 0.00E+00 1.20E+01 ESE 2.00E+00 5.00E+00 1.00E+00 0.00E+00 0.00E+00 0.00E+00 8.00E+00 SE 3.00E+00 7.00E+00 1.00E+00 1.00E+00 0.00E+00 0.00E+00 1.20E+01 SSE 5.00E+00 7.00E+00 6.00E+00 1.00E+00 0.00E+00 0.00E+00 1.90E+01 S 3.00E+00 9.00E+00 1.10E+01 2.00E+00 1.00E+00 0.00E+00 2.60E+01 SSW 1.00E+00 5.00E+00 7.00E+00 1.00E+01 3.00E+00 0.00E+00 2.60E+01 SW 4.00E+00 6.00E+00 6.00E+00 4.00E+00 0.00E+00 '0.00E+00 2.00E+01 WSW 1.00E+00 7.00E+00 1.30E+01 4.00E+00 0.00E+00 2.00E+00 2.70E+01 W 3.00E+00 4.00E+00 1.60E+01 7.00E+00 2.00E+00 0.00E+00 3.20E+01 WNW 0.00E+00 6.00E+00 1.50E+01 8.00E+00 3.00E+00 4.00E+00 3.60E+01 NW 1.00E+00 1.10E+01 1.20E+01 4.00E+00 1.00E+00 0.00E+00 2.90E+01 NNW 0.00E+00 6.00E+00 1.00E+01 4.00E+00 0.00E+00 0.00E+00 2.00E+01 Total 3.30E+01 1.00E+02 1.35E+02 5.10E+01 1.00E+01 6.00E+00 3.35E+02 Periods of Calm (Hours): 2.00E+00 Hours ofInvalid Data: 0.00E+00 33
TABLE 10. Pane 3 of 8 l JOINT WIND FREQUENCY DISTRIBUTION BY STABILITY CLASS < Data Period: January 1,1997 - December 31,1997 STABILITY CLASS C 60 METER (All tabled values are Hours) SECTOR 13 mph 4-7 mph 8-12 mph 13-18 mph 19-24 mph >24 mph TOTAL N 0.00E+00 1.10E+01 1.50E+01 9.00E+00 0.00E+00 0.00E+00 3.50E+01 NNE 2.00E+00 4.00E+00 9.00E+00 7.00E+00 2.00E+00 0.00 E+00 2.40E+01 l NE 5.00E+00 4.00E+00 3.00E+00 4.00E400 0.00E+00 1.00E+00 1.70E+01 ENE 5.00E+00 6.00E+00 7.00E+00 1.00E+00 0.00E+00 2.00E+00 2.10E+01 E 2.00E+00 3.00E+00 2.00E+00 2.00E+00 1.00E+00 0.00E+00 1.00E+01 ESE 0.00E+00 9.00E+00 8.00E+00 1.00E+00 2.00E+00 0.00E+00 2.00E+01 SE 4.00E+00 4.00E+00 3.00E+00 0.00E+00 2.00E+00 2.00E+00 1.50E+01 SSE 5.00E+00 3.00E+00 4.00E+00 1.00E+00 0.00E+00 0.00E+00 1.30E+01 S 2.00E+00 2.00E+00 6.00E+00 3.00E+00 6.00E+00 3.00E+00 2.20E+01 SSW 0.00E+00 4.00E+00 9.00E+00 1.20E+01 3.00E+00 3.00E+00 3.10E+01 SW 1.00E+00 2.00E+00 6.00E+0c 1.20E+01 1.00E+00 0.00E+00 2.20E+01 WSW 1.00E+00 4.00E+00 1.00E+01 7.00E+00 4.00E+00 1.00E+00 2.70E+01 W 2.00E+00 6.00E+00 1.40E+01 1.00E+01 7.00E+00 7.00E+00 4.60E+01 WNW 0.00E+00 2.00E+00 8.00E+00 7.00E+00 5.00E+00 5.00E+00 2.70E+01 NW 2.00E+00 8.00E+00 7.00E+00 4.00E+00 4.00E+00 2.00E+00 2.70E+01 NNW 1.00E+00 7.00E+00 8.00E+00 7.00E+00 0.00E+00 0.00E+00 2.30E+01 Total 3.20E+01 7.90E+01 1.19E+02 8.70E+01 3.70E+01 2.60E+01 3.80E+02 Periods of Calm (Hours): 1.00E+00 Hours of Invalid Data: 0.00E+00 10 METER (All tabled values are Hours) SECTOR 1-3 mph 4-7 mph 812 mph 13-18 mph 19-24 mph >24 mph TOTAL N 1.00E+00 8.00E+00 1.90E+01 3.00E+00 0.00E+00 0.00E+00 3.10E+01 NNE 2.00E+00 9.00E+00 9.00E+00 3.00E+00 0.00E+00 0.00E+00 2.30E+01 NE 6.00E+00 7.00E+00 3.00E+00 2.00E+00 0.00E+00 0.00E+00 1.80E+01 ENE 6.00E+00 8.00E+00 3.00E+00 0.00E+00 0.00E+00 0.00E+00 1.70E+01 E 5.00E+00 9.00E+00 3.00E+00 0.00E+00 0.00E+00 0.00E+00 1.70E+01 ESE 1.00E+00 7.00E+00 7.00E+00 0.00E+00 0.00E+00 0.00E+00 1.50E+01 SE 3.00E+00 5.00E+00 9.00E+00 1.00E+00 0.00E+00 0.00E+00 1.80E+01 SSE 3.00E+00 4.00E+00 6.00E+00 2.00E+00 0.00E+00 0.00E+00 1.50E+01 S 2.00E+00 1.30E+01 1.20E+01 5.00E+00 1.00E+00 0.00E+00 3.30E+01 SSW 3.00E+00 3.00E+00 1.40E+01 9.00E+00 1.00E+00 0.00E+00 3.00E+01 SW 0.00E+00 4.00E+00 1.10E+01 2.00E+00 0.00E+00 ' O.00E+00 1.70E+01 WSW 2.00E+00 5.00E+00 9.00E+00 6.00E+00 0.00E+00 0.00E+00 2.20E+01 W 2.00E+00 5.00E+00 2.10E+01 9.00E+00 7.00E+00 1.00E+00 4.50E+01 WNW 0.00E+00 5.00E+00 1.00E+01 6.00E+00 2.00E+00 3.00E+00 2.60E+01 NW 3.00E+00 1.10E+01 1.10E+01 3.00E+00 2.00E+00 0.00E+00 3.00E+01 NNW 3.00E+00 7.00E+00 1.10E+01 2.00E+00 0.00E+00 0.00E+00 2.30E+01 Total 4.20E+01 1.10E+02 1.58E+02 5.30E+01 1.30E+01 4.00E+00 3.80E+02 Periods of Calm (Hours): 1.00E+00 Hours of Invalid Data: 0.00E+00 34 l
TAllLE 10. Pane 4 of 8 JOINT WIND FREQUENCY DISTRIllUTION I!Y STAllILITY CLASS Data Period: January 1,1997 December 31,1997 STAlllLITY CLASS D 60 METER (All tabled values are Hours) SECTOR 1-3 mph 4-7 mph 8-12 mph 1318 mph 19 24 mph >24 mph TOTAL N 7.00E+00 3.30 E+01 1.05E+02 6.50E+01 1.10E+01 5.00E+00 2.2GE+02 NNE 7.00E+00 3.00E+01 5.80E+01 6.00E+01 2.90 E+01 2.50E+01 2.09E+02 NE 4.00E+00 2.30E+01 3.40E+01 7.20E+01 5.60E+01 1.90E+01 2.08E+02 ENE 1.40E+01 2.00E+01 3.60E+01 6.40E+01 4.30E+01 3.00E+01 2.07E+02 E 1.00E+01 4.30E+01 5.00E+01 2.40E+01 1.60E+01 1.00E+00 1.44 E+02 ESE 9.00E+00 5.40E+01 4.00E+01 5.00E+00 0.00E+00 0.00E+00 1.08E+02 SE 3.00E+00 2.20E+01 1.30E+01 1.50E+01 2.00E+00 3.00E+00 5.80E+01 SSE 4.00E+00 1.80E+01 3.90E+01 3.90E+01 1.90E+01 1.00E+01 1.29E+02 S 3.00E+00 1.10E+01 4.00E+01 6.20E+01 2.60E+01 1.70E+01 1.59E+02 SSW 4.00E+00 2.20E+01 2.80E+01 8.10E+01 2.50E+01 1.20E+01 1.72E+02 SW 6.00E+00 2.80E+01 3.20E+01 2.70E+01 1.30E+01 9.00E+00 1.15E+02 WSW 1.30E+01 2.80E+01 6.40E+01 3.30E+01 2.80E+01 1.40E+01 1.80E+02 W 9.00E+00 1.70E+01 5.50E+01 9.90E+01 5.10E+01 5.70E+01 2.88E+02 WNW 5.00E+00 2.00E+01 6.80E+01 1.05E+02 5.10E+01 2.20E+01 2.71 E+02 NW 5.00E+00 3.40E+01 5.40E+01 6.90E+01 4.90E+01 6.00E+00 2.17E+02 NNW 1.10E+01 3.90E+01 5.70E+01 5.60E+01 1.30E+01 1.00E+01 1.86E+02 Total 1.14 E+01 4.42E+02 7.73E+02 8.76E+02 4.32E+02 2.40E+02 2.88E+03 Periods of Calm (Hours): 5.00E+00 Hours ofInvalid Data: 0.00E+00 10 METER (All tabled values are Hours) SECTOR 1-3 mph 4-7 mph 8-12 mph 1318 mph 19-24 mph >24 mph TOTAL N 1.50E+01 7.30E+01 1.21E+02 4.30E+01 1.20E+01 0.00E+00 2.64 E+02 NNE 1.70E+01 6.10E+01 9.60E+01 3.60E+01 4.00E+00 0.00E+00 2.14 E+02 NE 1.40E+01 4.00E+01 6.80E+01 4.20E+01 1.00E+00 0.00E+00 1.65E+02 ENE 2.50E+01 6.40E+01 7.10E+01 1.40E+01 1.00E+00 0.00E+00 1.75E+02 E 2.30E+01 6.70E+01 2.30E+01 0.00E+00 0.00E+00 0.00E+00 1.13E+02 ESE 1.50E+01 8.10E+01 7.00E+00 1.00E+00 0.00E+00 0.00E+ 00 1.04 E+02 ! SE 5.00E+00 3.50E+01 2.00E+01 1.00E+01 0.00E+00 0.00E+00 7.00E+01 SSE 9.00E+00 7.00E+01 9.20E+01 1.80E+01 1.00E+00 1.00E+00 1.91E+02 S 8.00E+00 4.20E+01 7.10E+01 3.00E+01 7.00E+00 1.00E+00 1.59E+02 ; SSW 1.00E+01 3.40E+01 6.00E+01 3.40E+01 4.00E+00 0.00E+00 1.42E+02 SW 1.10E+01 3.50E+01 3.80E+01 1.00E+01 2.00E+00 1.00E+00 9.70E+01 WSW 2.30E+01 4.90E+01 7.80E+01 3.60E+01 3.00E+00 4.00E+00 1.93 E+02 W 9.00E+00 5.00E+01 1.13E+02 8.90E+01 4.10E+01 1.00E+01 3.12E+02 WNW 7.00E+00 5.30E+01 1.17E+02 1.06E+02 2.40E+01 9.00E+00 3.16E+02 NW 8.00E+00 5.30E+01 5.20E+01 5.70E+01 6.00E+00 0.00E+00 1.76E+02 NNW 1.30E+01 6.20E+01 8.40E+01 2.50E+01 2.00E+00 0.00E+00 1.86E+02 Total 2.12E+02 8.69E+02 1.11E+03 5.51 E+02 1.08E+02 2.60E+01 2.88E+03 Periods of Calm (Hours): 5.00E+00 Hours ofInvalid Data: 0.00 E+00 35
l TABLE 10. Pace 5 of 8 j JOINT WIND FREQUENCY DISTRIBUTION BY STABILITY CLASS Data Period: January 1,1997 - December 31,1997 j STABILITY CLASS E j 60 METER (All tabled values are Hours) SECTOR 1-3 mph 4-7 mph 8-12 mph 13-18 mph 19 24 mph >24 mph TOTAL N 1.00E+01 1.50E+01 5.40E+01 4.00E+01 1.00E+00 0.00E+00 1.20E+02 NNE 2.00E+00 1.30E+01 2.40E+01 6.00E+01 1.90 E+01 1.00E+00 1.19 E+02 NE 6.00E+00 1.50E+01 4.60E+01 5.00E+01 4.00E+00 0.00E+00 1.21 E+02 ENE 2.00E+00 1.50E+01 2.50 E+01 4.20E+01 1.60E+01 0.00E+00 1.00E+02 E 1.20E+01 1.40E+01 2.90E+01 2.60E+01 0.00E+00 0.00E+00 8.10E+01 ESE 1.10E+01 2.90E+01 3.20E+01 1.60E+01 1.00E+00 2.00E+00 9.10E+01 SE 6.00E+00 3.50E+01 3.10E+01 3.00E+01 1.10E+01 4.00E+00 1.17E+02 SSE 3.00E+00 1.90E+01 6.10E+01 6.40E+01 2.00E+01 1.10E+01 1.78E+02 S 4.00E+00 1.40E+01 4.20E+01 1.02E+02 4.90E+01 4.20E+01 2.53E+02 l SSW 4.00E+00 1.10E+01 3.50E+01 1.37E+02 6.20E+01 2.90E+01 2.78E+02 SW 4.00E+00 9.00E+00 5.20E+01 7.80E+01 1.70E+01 1.00E+00 1.61E+02 WSW 3.00E+00 1.70E+01 3.40E+01 3.10E+01 1.10E+01 1.00E+00 9.70E+01 W 3.00E+00 1.90E+01 2.10E+01 3.30E+01 2.90E+01 1.70E+01 1.22E+02 WNW 1.00E+00 1.10E+01 3.20E+01 4.40E+01 1.40E+01 3.00E+00 1.05E+02 NW 5.00E+00 2.70E+01 4.50E+01 2.00E+01 1.00E+00 0.00E+00 9.80E+01 NNW 3.00E+00 2.50E+01 4.40E+01 1.20E+01 3.00E+00 2.00E+00 8.90E+01 Total 7.90E+01 2.88E+02 6.07E+02 7.85E+02 2.58E+02 1.13E+02 2.13E+03 Periods of Calm (Hours): 5.00E+00 Hours ofInvalid Data: 0.00E+00 l 10 METER (All tabled values are Hours) SECTOR 1-3 mph 4 7 mph 8-12 mph 13-18 mph 19 24 mph >24 mph TOTAL N 1.60E+01 8.60E+01 4.50E+01 8.00E+00 0.00E+00 0.00E+00 1.55E+02 NNE 1.70E+01 2.10E+01 3.60E+01 0.00E+00 0.00E+00 0.00E+00 7.40E+01 NE 2.40E+01 6.50E+01 1.50E+01 1.00E+00 0.00E+00 0.00E+00 1.05E+02 ENE 2.60E+01 5.60E+01 1.00E+01 0.00E+00 0.00E+00 0.00E+00 9.20E+01 l E 2.80E+01 6.50E+01 3.00E+00 0.00E+00 0.00E+00 0.00E+00 9.60E+01 i ESE 4.70E+01 6.90E+01 1.00E+01 1.00E+00 0.00E+00 0.00E+00 1.27 E+02 SE 2.80E+01 8.70E+01 3.50E+01 6.00E+00 0.00E+00 0.00E+00 1.56E+02 ; SSE 2.10E+01 1.14 E+02 6.90E+01 1.30E+01 0.00E+00 0.00E+00 2.17E+02 S 1.90E+01 5.90E+01 1.02E+02 5.10E+01 3.00E+00 0.00E+00 2.34 E+02 SSW 8.00E+00 4.60E+01 1.11E+02 5.40E+01 1.00E+00 0.00E+00 2.20E+02 l SW 1.20E+01 7.00E+01 3.40E+01 7.00E+00 0.00E+00 '0.00E+00 1.23E+02 , WSW 1.40E+01 3.00E+01 4.80E+01 1.20E+01 0.00E+00 0.00E+00 1.04 E+02 W 1.60E+01 3.10E+01 3.70E+01 4.10E+01 1.00E+00 0.00E+00 1.26E+02 WNW 1.50E+01 4.30E+01 4.20E+01 7.00E+00 0.00E+00 0.00E+00 1.07E+02 l NW 1.80E+01 5.70E+01 1.50E+01 1.00E+00 0.00E+00 0.00E+ 00 9.10E+01 NNW 1.40E+01 5.90E+01 2.30E+01 2.00E+00 0.00E+00 0.00E+00 9.80E+01 Total 3.23E+02 9.58E+02 6.35E+02 2.04 E+02 5.00E+00 0.00E+00 2.13 E+03 Periods of Calm (Hours): 1.00E+01 Hours ofInvalid Data: 0.00E+00 36
. ._ __d
TAlli,E 10. Pane 6 of 8 JOINT WIND FREQUENCY DISTRIBUTION HY STABILITY CLASS Data Period: January 1,1997 - December 31,1997 STABILITY CLASS F 60 METER (All tabled values are Hours) SECTOR 1-3 mph 4-7 mph 8-12 mph 13-18 mph 19-24 mph >24 mph TOTAL N 2.00E+00 1.10E+ 01 1.10E+01 8.00E+00 0.00E+00 0.00E+00 3.20E+01 NNE 1.00E+00 4.00E+ 00 1.00E+01 1.60E+01 0.00E+00 0.00E+00 3.10E+01 NE 3.00E+00 0.00E+00 3.20E+01 2.70E+01 2.00E+ 00 0.00E+00 6.40E+01 ENE 1.00 E+00 1.00E+00 2.20E+01 1.10E+01 0.00E+00 0.00E+00 3.50E+01 E 3.00E+00 1.20E+01 1.90E+01 1.80E+01 3.00E+00 0.00E+00 5.50E+01 ESE 4.00E+00 2.40E+01 1.30E+01 5.00E+00 0.00E+00 0.00E+00 4.60E+01 SE 2.00E+00 1.50Fs+01 1.70E+01 1.00E+01 2.00E+00 0.00E+00 4.60E+01 SSE 0.00E+00 4.00E+ 00 2.10E+01 1.20E+01 0.00E+00 0.00E+00 3.70E+01 S 0.00E+00 2.00E+00 3.20E+01 4.90E+01 1.00E+00 0.00E+00 8.40E+01 SSW 1.00E+00 9.00E+00 1.60E+01 5.20E+01 7.00E+00 0.00E+00 8.50E+01 SW 1.00E+00 6.00E+00 1.80E+01 4.60E+01 3.00E+00 0.00E+00 7.40E+01 WSW 4.00E+00 5.00E+00 1.40E+01 1.90E+01 9.00E+00 0.00E+00 5.10E+01 W 3.00E+00 7.00E+00 2.10E+01 5.00E+00 0.00E+00 0.00E+00 3.60E+01 WNW 4.00E+00 8.00E+00 1.40E+01 5.00Fs+00 1.00E+00 0.00E+00 3.20E+01 NW 2.00E+00 8.00E+00 1.40E+01 7.00E+00 0.00E+00 0.00E+00 3.10E+01 NNW 3.00E+00 1.10E+01 1.80E+01 9.00E+00 0.00E+00 0.00E+00 4.10E+01 Total 3.40E+01 1.27E+02 2.92E+02 2.99E+02 2.80E+01 0.00E+00 7.80E+02 Periods of Calm (Hours): 2.00E+00 Hours ofInvalid Data: 0.00E+00 10 METER (All tabled values are hours) SECTOR 1-3 mph 4-7 mph 8-12 mph 13-18 mph 19-24 mph >24 mph TOTAL N 1.60E+01 2.30E+01 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.90E+01 NNE 1.10E+01 2.30E+01 0.00E+00 0.00E+00 0.00E+ 00 0.00E+00 3.40E+01 NE 3.00E+01 5.20E+01 1.00E+00 0.00E+00 0.00E+00 0.00E+00 8.30E+01 ENE 2.80E+01 1.30E+01 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.10E+01 E 2.10E+01 2.50E+01 0.00E+00 0.00E+00 0.00E+00 0.00E+ 00 4.60E+01 ESE 2.50E+01 3.70E+01 0.00Et00 0.00E+00 0.00E+00 0.00E+00 6.20E+01 SE 2.70E+01 3.20E+01 0.00E+00 0.00E+ 00 0.00E+00 0.00E+00 5.90E+01 SSE 1.10E+01 3.60E+01 4.00E+00 0.00E+00 0.00E+00 0.00E+00 5.10E+01 S 1.00E+01 4.20E+01 4.00E+00 0.00E+00 0.00E+00 0.00E+00 5.60E+01 i SSW 8.00E+00 5.40E+01 1.50E+01 0.00E+00 0.00E+00 0.00E+00 7.70E+01 j SW 1.00E+01 3.70E+01 7.00E+00 0.00E+00 0.00E+00 ' 0.00E+00 5.40E+01 l WSW 2.30E+01 1.90E+01 1.30E+01 0.00E+00 0.00E+00 0.00E+00 5.50E+01 ! W 1.20E+01 1.50E+01 1.00E+00 0.00E+00 0.00E+00 0.00E+00 2.80E+01 WNW 1.00E+01 1.30E+01 4.00E+00 0.00E+00 0.00E+00 0.00E+00 2.70E+01 NW 7.00E+00 2.60E+01 1.00E+00 0.00E+00 0.00E+00 0.00E+00 3.40E+01 NNW 1.10E+01 1.90E+01 2.00E+00 0.00E+00 0.00E+00 0.00E+00 3.20E+01 Total 2.60E+02 4.66E+02 5.20E+01 0.00E+00 0.00Fs+00 0.00E+00 7.78E+02 Periods of Calm (Hours): 4.00E+00 Hours of Invalid Data: 0.00E+00 37
)
TABLE 10. Pace 7 of 8 JOINT WIND FREQUENCY DISTRIBUTION HY STABILITY CLASS Data Period: January 1,1997 - December 31,1997
' STABILITY CLASS G 60 METER (All tabled values are Hours)
SECTOR 13 mph 4 7 mph 812 mph 13-18 mph 19-24 mph >24 mph TOTAL N 6.00E+00 7.00E+00 4.00E+00 3.00E+00 0.00E+00 0.00E+00 2.00E+01 NNE 4.00E+00 5.00E+00 4.00E+00 3.00E+00 0.00E+00 0.00E+00 1.60E+01 NE 2.00E+00 7.00E+00 1.10E+ 01 2.00E+01 1.00E+00 0.00E+00 4.10E+01 ENE 2.00E+00 1.10E+01 1.30E+ 01 8.00E+00 0.00E+00 0.00E+00 3.40E+01 E 0.00E+00 1.00E+01 1.50E+01 6.00E+00 2.00E+00 0.00E+00 3.30E+01 ESE 3.00E+00 2.10E+01 9.00E+00 1.00E+00 0.00E+00 0.00E+00 3.40E+01 SE 2.00E+00 3.00E+00 1.00E+00 5.00E+00 0.00E+00 0.00E+00 1.10E+01 SSE 1.00E+00 6.00E+00 8.00E+00 8.00E+00 0.00E+00 0.00E+00 2.30E+01 S 0.00E+00 3.00E+00 1.10E+01 1.30E+01 0.00E+00 0.00E+00 2.70E+01 SSW 0.00E+00 1.00E+00 1.90E+01 8.00E+00 2.00E+00 0.00E+00 3.00E+01 SW 0.00E+00 1.00E+00 1.10E+01 6.00E+00 1.00E+00 0.00E+00 1.90E+01 WSW 0.00E+00 5.00E+00 7.00E+00 3.00E+00 0.00E+00 0.00E+00 1.50E+01 W 2.00E+00 4.00E+00 7.00E+00 2.00E+00 0.00E+00 0.00E+00 1.6'0E+01 WNW 1.00E+00 0.00E+00 4.00E+00 0.00E+00 0.00E+00 0.00E+00 5.00E+00 NW 2.00E+00 1.00E+01 6.00E+00 1.00E+00 0.00E+00 0.00E+00 1.90E+01 NNW 4.00E+00 4.00E+00 1.00E+01 4.00E+00 0.00E+00 0.00E+00 2.20E+01 l Total 2 90E+01 9.80E+01 1.40E+02 9.10E+01 6.00E+00 0.00E+00 3.64 E+02 Periods of Calm (Hours): 3.00E+00 Hours ofInvalid Data: 0.00E+00 10 METER (All tabled values are Hours) SECTOR 1-3 mph 4-7 mph 8-12 mph 13-18 mph 19-24 mph >24 mph TOTAL N 1.70E+01 1.70E+01 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.40E+01 NNE 2.00E+01 1.00E+01 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.00E+01 l NE 3.10E+01 1.90E+01 0.00E+00 0.00E+00 0.00E+00 0.00E+00 5.00E+01 ENE 1.90E+01 4.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 2.30E+01 E 1.20E+01 8.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 2.00E+01 ESE 1.40E+01 2.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.60E+01 SE 1.40E+01 1.70E+01 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.10E+01 SSE 1.30E+01 2.00E+01 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.30E+01 S 1.10E+01 9.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 2.00E+01 SSW 1.60E+01 7.00E+00 2.00E+00 0.00E+00 0.00E+00 0.00E+00 2.50E+01 i SW 8.00E+00 4.00E+00 0.00E+00 0.00E+00 0.00E+00 '0.00E+00 1.20E+01 WSW 5.00E+00 4.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 9.00E+00 W 7.00E+00 3.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.00E+01 WNW 3.00E+00 5.00E400 0.00E+00 0.00E+00 0.00E+00 0.00E+00 8.00E+00 NW 1.40E+01 1.10E+01 0.00E+00 0.00E+00 0.00E+00 0.00E+00 2.50E+01 NNW 1.20E+01 5.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.70E+01 Total 2.16E+02 1.45 E+02 2.00E+00 0.00E+00 0.00E+00 0.00E+00 3.63E+02 Periods of Calm (Hours): 4.00E+00 Hours ofInvalid Data: 0.00E+00 38
TAlli,E 10. Pane 8 of 8 JOINT WIND FREQUENCY DISTRHlUTION IlY STABILITY CLASS Data Period: January 1,1997 - December 31,1997 All STAllli,lTY CLASSES 60 METER (All tabled values are Percents) SECTOR 1-3 mph 4-7 mph 8-12 mph 1318 mph 19 24 mph >24 mph TOTAL N 2.97E-01 1.00E+00 2.92E4 00 1.71 E+00 1.37E-01 5.71E 02 6.13 E+00 NNE 1.94 E-01 7.53 E.01 1.51 h+00 2.04 E+00 6.96E-01 2.97E-01 5.49E+00 NE 2.51 E-01 8.33E 01 1.61 E4 00 2.19 E+00 7.99E 01 2.63E-01 5.95E+00 l ENE 3.31 E.01 8.90E-01 1.4 7 E+00 1.66E+00 7.31 E-01 4.00E-01 5.4 8E+00 E 4.11 E-01 1.22E+00 1.76E+00 1.00E+00 2.85 E.01 2.28E-02 4.70E+00 ESE 4.11 E-01 1.79E+00 1.19E+00 3.31 E-01 3.42E 02 3.42E-02 3.79E+00 i SE 4.45E-01 1.23E+00 9.36E.01 7.42 E-01 1.94 E-01 1.37E-01 3.69E+00 { SSE 2.40E-01 8.68E-01 1.85E+00 1.50E+00 4.79E-01 2.74 E-01 5.21 E+00 l S 2.51 E-01 8.33E-01 2.10E+00 2.96 E+ 00 1.11 E+00 7.53E 01 8.00E+00 SSW 1.83E-01 1.16E+00 1.83 E+00 3.86E+00 1.31 E+00 5.48E-01 8.89E+00 SW 1.71E-01 8.11E 01 1.84 E+00 2.41 E+00 5.37E-01 1.60E-01 5.92 F,+00 WSW 3.20E-01 9.93E-01 1.91 E+00 1.26E+00 6.62E-01 3.20E 01 5.46E+00 W 2.51E-01 7.99E-01 1.66E+00 2.07E+00 1.29E+00 9.82E-01 7.04 E+00 3 l WNW 1.49E-01 6.62E 01 1.78E+00 2.36E+00 1.08E+00 4.68E-01 6.51 E+00 NW 1.94E-01 1.27E+00 1.86E+00 1.70E+00 7.65E-01 1.83 E-01 5.97E+00 l NNW 2.51 E-01 1.19E+00 1.95E+00 1.42E+00 2.17E-01 1.37E-01 5.16E+00 l Total 4.35E+00 1.63E+01 2.82E+01 2.92E+01 1.03E+01 5.03 E+00 9.34 E+01 Periods of Calm (Hours): 17 Hours ofInvalid Data: 0 Hours of Good Data: 8.198E+03 94.2% of Total Hours 10 METER (All tabled values are Percents) SECTOR 13 mph 4-7 mph 8-12 mph 13-18 mph 19-24 mph >24 mph TOTAL N 7.99E-01 2.60E+00 3.03E+00 7.88E-01 1.37E-01 0.00E+00 7.35 E+00 NNE 7.99E-01 1.71 E+00 2.07E+00 5.37E-01 4.57E-02 0.00E+00 5.16E+00 NE 1.24 E+00 2.49E+00 1.27E+00 6.51 E-01 1.14 E-02 0.00E+00 5.66E+00 ENE 1.28E+00 1.92 E+00 1.06E+00 1.60E-01 1.14 E-02 0.00E+00 4.43E+00 E 1.21E+00 2.56E+00 5.25E-01 0.00E+00 0.00E+00 0.00E+00 4.29E+00 ESE 1.28E+00 2.80E+00 3.54 E-01 2.28E-02 0.00E+00 0.00E+00 4.45E+00 SE 1.04E+00 2.65E+ 00 1.03 E+00 2.28E-01 0.00E+00 0.00E+00 4.94 E+00 SSE 8.11 E-01 3.78E+00 2.49E+00 4.79E-01 2.28E-02 1.14 E-02 7.59E+00 S 6.96E-01 2.43 E+00 2.83E+00 1.13 E+00 1.60E-01 1.14 E-02 7.26E+00 SSW 5.71E 01 2.00E+00 3.05 E+00 1.43E+00 1.26E-01 0.00E+00 7.17E+00 SW 5.25E-01 1.99E+00 1.56E+00 4.91 E-01 3.42E-02 2.28E-02 4.62E+00 WSW 8.11 E-01 1.56E+00 2.10E+ 00 7.42 E-01 4.57E-02 1.26E-01 5.39E+00 W 6.05 E-01 1.48E+00 2.50E+00 2.02E+00 6.39 E-01 1.48E-01 7.40E+ 00 WNW 4.11 E-01 1.56E+00 2.59E+00 1.80E+ 00 5.48E-01 1.83E-01 7.10E+00 NW G.05E-01 2.18E+00 1.43 E+00 9.82E 01 1.14 E-01 0.00E+00 5.31E+00 NNW 6.16E-01 1.93E &OO 1.96 E+00 5.82 E-01 2.28 E-02 0.00E+00 5.11 E+00 Total 1.33E+01 3.56E+01 2.98E+01 1.20E+01 1.92E+00 - 5.02E-01 9.32E+01 Periods of Calm (Hours): 30 Hours ofInvalid Data: 0 Hours of Good Data: 8.198E+03 = 94.2% of Total Hours 39
SECTION 6 DOSE MEASUREMENTS AND ASSESSMENTS TABLE 11 MAXIMUM
- OFFSITE DOSES AND DOSE COMMITMENTS TO MEMBERS OF THE PUBLIC Data Period: January 1,1997 - December 31,1997 A. Waterborne Effluents (mrem):
Organ 0.00E.00 Total Body 0.00E-00 B. Airborne Effluents:
- 1. Iodines and particulates (mrem):
Organ 1.18E-03' Total Body 7.44 E-031
- 2. Noble Gases (mrad):
Gamma 0.00E+00' 2 Beta 0.00E+00 C. Direct Radiation (mrem): O.00E+00 1 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.
2 Organ dose is to the Adult Gastrointestinal System via the inhalation, ground plane, meat and vegetation pathways. Total Body dose is to the Child Gastrointestinal System via the inhalation, ground plane, meat and vegetation pathways. Noble gas total body doses also added to organ dose. Calculated at 1.50 km in the North direction using the methodology i contained in the CPS ODCM. 2 Dose to total body and skin of all occupants regardless of age. Calculated at 1.50 km in the North direction using the methodology contained in the CPS ODCM. 40
DOSES TO M EMilEllS OF TI{ E PUllLIC WITillN TIIE SITE 110UNDAltY CPS Offsite Dose Calculation Manual section 7.2 requires that the Itadioactive Effluent Itelease Iteport include an assessment of the radiation doses from radioactive liquids and gaseous effluents to MEMI1 Ells OF TIIE PUllLIC due to their activities inside the SITE IlOUNDAltY. Within the CPS site boundary there are seven areas which are open to members of the public as identified by CPS ODCM Table 3.4 4 (see Figure 4): The Department of Natural Itesources Itecreation Area at 1.287 kilometers (0.8 miles) in the ESE sector A road at 0.495 kilometers (0.3 miles) in the SE sector A residence at 2.736 kilometers (1.7 miles) in the SSE sector A residence at 1.219 kilometers (0.8 miles) in the SW sector Agricultural acreage at 1.372 kilometers (0.9 miles) in the SSW sector A residence at 2.414 kilometers (1.5 miles) in the WSW sector A portion of Clinton Lake at 0.335 kilometers (0.2 miles) in the NW sector At all of the above locations, the plume, inhalation and ground. plane exposure pathways are used for dose calculations. No other exposure pathways were identified by the 1997 Annual Land Use Census. All dose calculations were performed using the methodology contained in the CPS ODCM. I 1 l 41
FIGURE 4 AREAS WITHIN THE. CPS SITE BOUNDARY OPEN TO MEMBERS OF TIIE PUBLIC 1 CLINTON 83
~
.. / -
-M* [' ,
,,,,,, WAPELLA MAROA
- r. . ...... .... ....... .. n ,.. . . .
y, e e...... <. . .u . .. . . ........, ......
. .......... ., c...........
, ....,. . a. n s.. .. . . .... ..... ................
6
- d
" 6 g
8 rp o , E 1 'd e\
(t y [g ' PC.P.S. sxcon Co. WELDON g 4 , PIATT CO. b g CISCO
\
De 1 hy ' co o Co. '
/
FARMER / I l l DELAND CITY "//
'/
TO ' CHAMPAIGN . 7d 1 42 t.
TAlli,E 12 CALCUI,ATED DOSES TO MEMHERS OF THE PUllLIC DUltlNG USE OF THE DEPARTMENT OF NATURAL RESOURCES RECREATION AREA IN THE EAST-SOUTHEAST SECTOR WITIIIN THE CPS SITE BOUNDARY Data Period: January 1,1997 - December 31,1997 hposure Pathway Otrga_n_s Dose (mitem) plume
- total body 0.00E+00 skin 0.00E+00 ground plane
- total body 2.53E-05 skin 2.98E-05 inhalation; age group highest organ doses:
teen lung 7.62E-07 adult lung 6.71 E-06 - child lung 6.09E-06 infant lung 3.54E-06 o Doses via these pathways are not dependent upon age-group. 1 43 { j
TABLE 13 CALCULATED DOSES TO MEMBEllS OF THE PUBLIC DUltlNG USE OF THE ItOAD IN THE SOUTH EAST SECTOR WITHIN THE CPS SITE BOUNDARY Data Period: January 1,1997 - December 31,1997 Exposure Pathway Ornans Dose (mrem)
, plume
- total body 0.00E+00 skin 0.00E+00 ground plane
- total body 5.10E-06 skin 6.00E-06 inhalation; age group highest organ doses:
teen lung 1.59E-06 adult lung 1.55E-06 child lung 1.40E-06 infant lung - 8.10E-07 Doses via these pathways are not dependent upon age group. l 44 i-
TAIll,E 14 - l CALCULATED DOSES FOlt TIIE ITESIDENTS IN TIIE SOUTil-SOUTilEAST SECTOlt WITHIN - Tile CPS SITE IlOUNDAltY Data Period: January 1,1997 December 31,1997 Exnosure Pathway Ortans Dose (mrem) plume
- total body 0.00E+00 skin 0.00E+00 ground plane
- total body 1.67E-05 ,
skin 1.97E 05 l I inhalation; age group highest organ doses: (1) adult lung 8.77E-06 teen lung 0.00E+00 child lung 0.00E+00 infant lung 0.00E+00 s Doses via these pathways are not dependent upon age-group. (1) A value of 0.00E+00 indicates that no individual of this age group resides at this receptor l location. l l i l 1
]
45
TABLE 15 CALCULATED DOSES FOR THE RESIDENTS IN THE SOUTHWEST SECTOR WITHIN THE CPS SITE BOUNDARY Data Period: January 1,1997 - December 31,1997 Exposure Pathway Oreans Dose (mrem) plume
- total body 0.00E+00 skin 0.00E+00 ground plane
- total body 6.86E-05 skin 8.07E 05 inhalation; age group highest organ doses: (1) adult lung 4.09E-05 teen lung 0.00E+00 child lung 0.00E+00 infant lung 0.00E+00
- Doses via these pathways are not dependent upon age-group.
(1) A value of 0.00E+00 indicates that no individual of this age group resides at this receptor location.
~
46 t
TAlli,E 16 CALCULATED DOSES TO MEMI3ERS OF THE PUBLIC DURING USE OF THE AGRICULTURAL ACREAGE l IN THE SOUTH SOUTHWEST SECTOR WITHIN THE CPS SITE BOUNDARY Data Period: January 1,1997 December 31,1997 Exposure Pathway Oreans Dose 6nRem) plume
- total body 0.00E+00 skin 0.00E+00 ground plane
- total body 6.30E 06 skin 7.41E-06 inhalation; age group highest organ doses:
teen lung 3.03E-06 adult lung 2.93E-06 child lung 2.67E-06
- infant lung 1.55E-06 i
l 0 l Doses via these pathways are not dependent upon age-group. I i 1 I l l i l l
\
47
TABLE 17 cal,CULATED DOSES FOR THE RESIDENTS IN THE WEST-SOUTHWEST SECTOR WITHIN TIIE CPS SITE BOUNDARY l Data Period: January 1,1997 - December 31,1997 Exposure Pathway OrhaAs Dose (mrem) plume
- total body 0.00E+00 skin 0.00E+00 ground plane
- total body 1.98E-05 skin 2.33E 05 inhalation; age group highest organ doses (1):
adult lung 1.14 E-05 teen lung 0.00E+00 child lung .0.00E+00 infant lung 0.00E+00 i Doses via these pathways are not dependent upon age-group. (1) A value of 0.00E+00 indicates that no individual of this age group resides at this receptor location.
'I 48 u_ _
l. TAllLE 18 CALCULATED DOSES TO MEMBEllS OF TIIE PUBLIC i DULLING USE OF CLINTON LAKE IN T11E I NoltTHWEST SECTOlt WITHIN TiiE CPS SITE BOUNDAltY Data Period: January 1,1997 December 31,1997 l Exposure Pathway Oreans Dose (mItem) i plume
- total body 0.00E+00 skin 0.00E+00 i i ground plane
- total body 5.55E-05 l skin 6.53E-05 inhalation; age group highest organ doses:
teen lung 7.11E-05 1 l adult lung 6.89E-05 child lung 6.26E-05 infant lung 3.63E-05 l o Doses via these pathways are not dependent upon age-group. l l 49
( l l SECTION 7 l CHANGES TO THE OFFSITE DOSE CALCULATION MANUAL I Changes to the Offsite Dose Calculation Manual are included as separate attachments. l l l I l l l i l l l 50
SECTION 8
. ODCM OPERATIONAL REQUIREMENT 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 Radioactive Effluent Release Report.
During 1997, there were 2 instances of radioactive liquid effluent instrumentation channels being inoperable for more than 30 days. These instances are documented on the following pages. 51
IRIX-PR037 Comnonent Coolina Water 1RIX-PR037 Component Cooling Water (CCW) Process Radiation Monitor was inoperable from 8/18/97 at 0005 to 9/17/97 at 2100. Below is a description of the related events, the root cause and the corrective actions to prevent recurrence. Chronology
. On August 6,1997 revision 15 of the ODCM is made effective. This revision places 1RIX.
PR037 CCW Process Radiation Monitor into the ODCM as part of the corrective action to Condition Report (CR) 1-96 10 260.
. On August 17,19971RIX-PR037 is calibrated by C&I under Preventative Maintenance Task PCIPRM237 in accordance with CPS No. 8640.06. However, since 1RIX PR037 is now an ODCM-required monitor, the calibration should have been performed in accordance with CPS No. 9437.62 which is used to calibrate ODCM liquid effluent radiation monitors. CPS No. 9437.62 does not currently address 1RIX-PR037 and requires revision to incorporate it.
An additional MWR (D73927) exists for a chattering relay. The System Manager asks if the C&I crew fixed the relay at the same time the calibrated the monitor. They did not. The monitor is maintained inoperable.
. CR 1-97-08156 is written identifying procedures (CPS Nos. 9911.24,9911.11, and 8640.06) which are not revised to support the ODCM change. The immediate action for this CR was to declare 1RIX PR037 inoperable. ODCM Operational requirement (OOR) 97-048 is entered on August 18,1997 at 0005 in accordance with CPS No. 1909.22
. On August 19,1997, MWR D73927 to replace chattering relay is approved for work.
. The chattering relay is replaced under MWR D73927 on September 2,1997.
. An Engineering Evaluation is written by the System Engineer describing the above situation and concludes that the calibration data obtained under CPS No. 8640.06 should be transferred to CPS No. 9437.62 " Liquid Process Radiation Monitor 1RIX-PR004 (5, 36,38,
- 39) Calibration" and IRIX PR037 declared operable. The logic used was that the calibration methodology and the acceptance criteria for both procedures are exactly the same. This argument is rejected by the Shift Supervisor, The Assistant Plant Manager-Operations, and the Assistant Director-Operations.
. The System Engineer submits a " scope add" request to re-perform the calibration using the revised CPS No. 9437.62 procedure. . The scope add request is disapproved by the Outage Scope Committee meeting on September 9,1997. . The System Engineer speaks directly to the Director-Planning and Scheduling and the work is added to the outage scope. . On September 10,1997, a revision to CPS No. 9437.62 is approved which allows calibration of 1RIX-PR037 under the appropriate procedure. . CR 1-97 09-181 is written identifying the failure to restore IRIX-PR037 to operable status within 30 days.
52
- The calibration of 11tlX. Plt 037 is re-performed under CPS No. 9437.62 and the monitor declared operable on September 17,1997 at 2100. OOlt 97 048 is exited, e 11tlX Pit 037 is inoperable for 740.92 hours (30.87 days).
Itoot Cause The root cause of this event is inadequate implementation of the ODCM revision. ODCM, revision 15 was implemented before supporting procedures were ready. The ODCM revision was not made known to affected departments which caused delays in getting the affected procedures revised to support the change. These delays caused the monitor to be inoperable for greater than 30 days. A potential contributing factor was the failure to get the calibration of IltlX-pit 037 added to the outage scope work in a timely manner. Corrective Actions The corrective action to prevent recurrence of this condition was to revise CPS No. 1800.00 "Itevising the ODCM", to add instructions to notify department heads of pending ODCM changes. This action has been completed and tested successfully with the implementation of ODCM revision 16. l 53
1RIX-PR036 Plant Service Water 1RIX-PR036, Plant Service Water (WS) Process Radiation Monitor was inoperable from 11/16/97, + to 01/03/98. Below is a listing of the troubleshooting steps followed to repair the monitor as well as the root cause and corrective actions to prevent recurrence.
. IRIX-PR036 began experiencing problems in communicating with the Central Control Terminal (CCT) in the Main Control Room). Maintenance Work Request D81531 was issued to correct the problem. . Control and Instrumentation (C&I) personnel obtained historical information on Communication Line B and on the monitors using Communication Line B. It was determined that more than one monitor had experienced similar problems as 1RIX PR036 over the last 12 months. Subsequently, the maintenance history of all components and parts that had been replaced was reviewed. . C&I began troubleshooting the repeater for Communication Line B. All data points were verified correct. Then, all monitor inputs were removed and the testing repeated, identifying several inaccuracies. . C&I attempted to repair the repeater. Failing this, a new repeater was installed after first verifying the new repeater worked on the bench. A known operable portable radiation monitor was connected to the Communication Line and operation observed for a period of time. . The other monitors serviced by Communication Line B were reworked and made operable. In addition, the correct operation of the repeater was verified after each monitor was returned to the Communication Line. . The old repeater was returned to the Vendor for determination of the problem and repair. . 1RIX PR036 was returned to the Communication Line and its' proper operation verified for 5 days.
i Root Cause The repeated failure of 1RIX-PR036 was the failure of C&I to correctly troubleshoot both the true i catse of the problem as well as the extent of the problem. Corrective Actions Specific informat' ion and lessons learned concerning this problem was provided to the C&l Technicians through briefing from the Supervisor C&I and the technician involved in the troubleshooting effort. In addition, requalification training will be provided to C&I technicians on the AR/PR system later this year. 1 l 54
SECTION 9 MAJOR CHANGES TO RADIOACTIVE WASTE TREATMENT SYSTEMS In accordance with the CPS ODCM section 7.2, licensee-initiated major changes to the liquid, gaseous or solid radioactive waste treatment systems shall be reported in the Radioactive Effluent llelease Report. No major changes to the Waste Treatment Systems were reviewed and approved during this reporting period. l l l l ( 55
SECTION 10 NEW LOCATIONS FOR DOSE CALCULATICN AND/OR ENVIRONME.NTAL l MONITORING In accordance with the CPS ODCM, new locations for dose calculations and/or environmenta3 monitoring identified by the Annual Land Use Census shall be reported in the Radioactive Effluent Release Report. The following is a summary of the 1997 Annual Land Use Census. 1.0 Nearest Residence The nearest resident identified in each of the 16 sectors are shown below: 1996 1997 SECTOR RESIDENT AGE GROUP RESIDENT AGE GROUP N DAUGHERTY CTA DAUGHERTY CTA NNE BROWN A BROWN A NE BARTIMUS CA BARTIMUS CA ENE DEFEBAUGH A DEFEBAUGH A E NIEDERER A NIEDERER A ESE EDWARDS ICA EDWARDS CA SE TWIST A TWIST TA SSE JACOBS A JACOBS A S DISNEY A DISNEY A SSW EHALT A EHALT A SW REYNOLDS A REYNOLDS A WSW LYNN A LYNN A W SANDERS TA SANDERS TA WNW LORD CTA HUSTED TA NW ENOS TA ENOS TA NNW CRABTREE A CRABTREE A (I)nfant (C)hild (T)een (A)dult 4 56
2.0 llroadleaf Garden Census , i Over 100 gardens within 5 miles were located in the 16 sectors surrounding CPS. Specifically I broad leaf vegetation was identified for this report. Other crops grown in this area were identified but will not be addressed in this report. The nearest garden identified in each of the 16 sectors are shown below: 1996 1997 SECTOR GARDENS AGE GROUPS GARDENS AGE GROUPS N DAUGHERTY CTA KOHLER A NNE BURTON A THRASHER A NE SPENCER CTA LARRY A ENE DEFEBAUGH A DEFEBAUGH A E BRATCHER A BRATCHER A ESE EDWARDS ICA HOLTZSCHER CA SE NONE N/A NONE N/A SSE WOOD C.T A WEST A S MARTIN A MARTIN A SSW WILLIAMS A WILLIAMS TA SW PARKER A PARKER CA WSW BURTON A THOMASON A W LANUM IA LANUM CA WNW STAPLETON A HUSTED TA NW RODRICK TA SHEAHAN A NNW COPE CA LORD A (I)nfant (C)hild (T)een (A)dult l l l i I 57 j
3.0 Milkine Animal Census Milking animals within 5 miles were located in 10 of the 16 sectors surrounding CPS. The cattle were used for nursing (nursing of calves) and were being used fer meat production (both own use and to be sold). There were no residents that milked their animals for human consumption. Milking animals were specifically identified for this report. Other livestock raised in this area were identified but will not be addressed in this report. The nearest milking animals identified in each of the 16 sectors are shown below: 1996 1997 SECTOR MILKING AGE GROUPS MILKING AGE GROUPS ANIMALS ANIMALS N MARX A DAUGHERTY CTA NNE LARRY A LARRY A NE NONE N/A SPENCER TA ENE DAWSON A DAWSON A . E NONE N/A NONE N/A ESE NONE N/A NONE N/A SE NONE N/A NONE N/A SSE MOODY A MOODY A S MARTIN A MARTIN A SSW WANTLAND A R.WANTLAND TA SW WANTLAND A ISSAC TA WSW BEST A BEST* A W MOODY CTA MOODY CTA WNW NONE N/A NONE N/A NW NONE N/A BASTING A NNW WILSON A WILSON A (I)nfant (C)hild (T)een (A)dult 4 58
SECTION 11 COltitECTIONS TO DATA REPORTED IN PitEVIOUS ItEPORTS There are no corrections to data included in previous reports. 59
1 1 l 1 CLINTON POWER STATION 1 l OFFSITE DOSE CALCULATION MANUAL
- REVISION 15 l
l l Issued: JULY 30,1997 l l t I
CPS NO. _1005xWiF002 l l SAFETY EVALUATION FORM l (8.3.1 1.a) LOG 97 - 15E_ REv. l (8.3.1.1.b) DOCUMENT EVALUATED: Offaite Dnam r' min ulation Manual 10DCMI REVISION: 15 j (8.3.1.1.c) TITLE: Offaite Dona Calculation ManualiODCMLChange i (8.3.1.1.d) DESCRIPTION AND IMPACT OF CHANGE ON LICENSING DOCUMENTS: This ravision to the ODCM incorporates both editorial and technical changes. ) The sditorial changes correct obvious typographical errors introduced by previous revisions to the ODCM. p Th2s3 changes include:
- 1) Revising Table 2.3-1, Table Notation "a" definition for " Delta T" to match the algorithm used by the c:ntrolled software.
l 2) Revised SR 3.4.1.1 and SR 3.4.1.2 to cross-reference the correct section numbers in the ODCM. l 3) Rsvised Table 3.4-1 to remove erroneous footnotes which were introduced when the table was . rsfcrmatted by a previous revision to the ODCM.
- 4) Revised Table 3.4-1, Table Notation "a" definition for " Delta T" to match the algorithm use ; oy the centrolled software.
l 6) Revised Table 3.4-1, Table Notation "4" to add a clarifying statement regarding monitor applicability.
- 6) Revised Table 3.9.1-2 to fix mis aligned table headings.
(continued) , (8.3.1.1.d)
REFERENCES:
- Offsite Dose Calculation Manual (ODCM)
- Table 1.1-1,1.2.2.8.3, 2.1, 2.3.1, Table 2.3-1, 2.3.5, 2.3.6, i Table 2.7-1, Table 2.7-2, 3.1, SR 3.4.1.1, SR 3.4.1.2, Table 3.41, 3.4.2, 3.4.3, Table 3.9.1-2, Table 3.9.2-1, 6.1, Table 6.1-1, 6.2, 9.2.6.1, 9.2.9.1, 9.2.9.2, 9.2.11, 9.2.11.1 .
! USAR Sections: 1.8,11.6, Table 11.5-1, Table 11.5 2, Table 16.2.4-3a Technical Specifications: 6.6.1, 6.6.4, 6.6.4.b, 6.6.2, 6.6.3
- ' Operati
- nal Requirements Manua; (ORM)i 6.8.4.c
! (:ontinued) I (8.3.1.1.h) Prepared by: d lwes Date: 7/A N y, g , Signature ] (8.3.2.2) Reviewed by: ^ ha
,. -3 -r Date: 7 E2^77 t
Name Signatuhe (8.3.3) Approved by: S,6 Abw M Me* Date: ~7/W I47
-19, A NamftMp u TJ Signature - l (8.3.4) FRG: h[fb *tM'St / Date 7/d[!O2
' Name ' Signat(re #
Rav. No. 1 1% CI OoW i J
I CLASS CODli. SNNNI l i CPS No.1005.06F003 ' (Rev.0) LOG _N _ _1_ REV. 4_. Page of _N_ SAFETY EVALUATION CONTINUATION SIIEET Document Evaluated: Provide the justification / references / explanation for all answers on cover sheet as follows (attach additional sheets, as necessary): ) l References (continued): Regulatory Guides: 1.21, 1.109, 1.111 NUREG-0133, NUREG-0473 Code of Federal Regulations (CFR): 10CFR20.1302: 10CFR20, Appendix B, Table 2, Column 2; 10CFR50.36a; 10CFR50 Appendix A; 10CFR50 Appendix I; 40CFR190 CR 1-96-10-260 SER Amendment No. 95 General Design Criteria (GDC) 60 and 64 CPS No. 3212.01 Description and impact (continued):
- 7) Revised Section 5.1, Remedial Requirement "c" to reference the correct report title in accordance with the associated Technical Specifications section.
- 8) Revised Table 5.1-1, Table Notation "a" to reference the correct report title in accordance with the associated Technical Specifications section.
- 9) Revised Section 5.2, Remedial Requirement "a" to reference the correct report title in accordance with the associated Technical Specifications section.
- 10) Revised Section 9.2.6.1 to add a description for variable "X" for consistency with the other variables in the equation.
- 11) Revised Sections 9.2.9.1 and 9.2.9.2 to add the word " meters" to the variable column heading.
- 12) Revised Section 9.2.11.1 to specify " elevated level" in accordance with Section 9.2.11 heading.
The editorial changes incorporated by this revision do not change the intent of the ODCM and are consistent with the regulatory requirements of 10CFR20.1302,10CFR50.36a,10CFR50 Appendix 1,40CFR190, and Technical Specifications. These changes maintain the levels of radioactivc effluent control required by these regulations and do not adversely impact the reliability of effluent, dose, or setpoint calculations. This revision to the ODCM contains the following technical changes: *
- 1) Revised Table 1.1 1 to add a clarifying footnote for composite samples.
- 2) Revised Section 2.3.1 to change the limit for liquid radioactive material released to unrestricted '
~
areps to match Technical Specification Ucensing Amendment 95, section 5.5.4.b.
- 3) Revised Section 2.3.5 to require sampling Component Cooling Water (CCW) prior to placing the Fuel Pool Heat Exchanger in the Shutdown Service Water (SX) cooling mode. Deleted the word
" batch" from the description of the release type to remove an incorrect description of the type of release.
(continued) N l t _ _ _ _ - - - _ - - - - -
CLASS CODE: SNNNI CPS NO.1005. 06F003 (Rev. 0) LOG - REV. Page 2 of 4 SAFETY EVALUATION CONTINUATION SIIEET Document Evaluated: offsite Dome calculation Manunucocui Provide the justification / references / explanation for all answers on cover sheet as follows (attach additional sheets, as necessary): Dsscription and Impact (continteed):
- 4) Added new Section 2.3.6 to include CCW PRM setpoints in the ODCM based on Condition Report (CR) 1-96-10-260 corrective actions.
- 5) Revised Table 2.71 to include CCW PRM monitoring instrumentation in accordance with CR 196-10-260 and new ODCM Section 2.3.6.
- 6) Revised Table 2.7-1 Remedial Requirement "2" to add the requirement for the " communication link" to be operable for considering the radioactive ligtiid effluent monitoring instrumentation as operable.
- 7) Revised Table 2.7 2 to include CCW PRM surveillance requirements in accordance with CR; 196-10-260 and new ODCM Section 2.3.6.
- 8) Revised Table 3.9.2-1 to reformat the table for clarity and to add approved alternate flow measuring devices for indicating SGTS flow rate.
The technical changes incorporated by this revision align the ODCM with Technical Specification 6.6.4.b liquid release limits, eliminate unnecessary sampling for the CCW when shutdown service w::ter (SX) D r.ot supplying cooling water to the fuel pool heat exchangers, add CCW PRMs to the monitoring program, specify that the communication links are included in PRM channel check operability, and add alternate flow rate measuring devices for the SGTS gaseous effluent monitoring instruments. These technical changes are consistent with the requirements of 10CFR20,10CFR50 Appendix A,10CFR50 Appendix 1,40CFR190, and Technical Specifications. Calculations for dose cnd alarm setpoints are not modified by these technical changes. There are no reductions in commitment associated with these editorial and technical changes. Justification: Part 1: The editorial and technical changes incorporated by this revision to the ODCM are not pertinent to . malfunctions of equipment important to safety (IS) which were evaluated as the design bases. The 1::chnical changes incorporated by this revision do not relate to operation of plant equipment, only to surveillance and monitoring of radioactive effluents and calculations of dose to the public. No safety-related or special scope equipment are affected by these changes. The probability of a malfunction of equipment IS and an increase in the consequences of a malfunction (specifically dose to unrestricted areas) are not applicable to these ODCM changes. (continued)
CLASS CODE: SNNNI CPS NO.1005.06F003 (Rev. 0) LOG - REV._ Page of 3 4 SAFETY EVALUATION CONTINUATION SHEET Document Evaluated: offaita Dose calculation Manual (OncMi Provide thejustification/ references / explanation for all answers on cover sheet as follows (attach additional sheets, as necessary): Justification (continued); Part II: The Clinton Power Station OFFSITE DOSE CALCULATION MANUAL (CPS-ODCM) provides the methodologies and parameters used by liiinois Power Company (IP) to assure compliance with the radioactive effluent dose limitations stated in 10CFR20,10CFR50 Appendix A (General Design Criteria 60 and 64),10CFR50 Appendix 1, and 40CFR190. The CPS-ODCM was prepared based on guidance provided in NUREG-0133, PREPARATION OFl RADIOLOGICAL EFFLUENT TECHNICAL SPECIFICATIONS FOR NUCLEAR POWER PLANTS (October 1978), and NUREG-0473, RADIOLOGICAL EFFLUENT TECHNICAL SPECIFICATIONS FOR BOILING ! WATER REACTORS (Draft 7, to Revision 3). This manual along with station procedures are used by CPS personnel to demonstrate compliance with the above referenced Federal Regulations. Based on a review of the SAR, there are no evaluated accidents associated with calculations for radioactive effluent dose. The ODCM is not used to operate equipment necessary to mitigate accidents. The ODCM provides calculations and methodologies to determine the extent of dose to unrestricted areas as a result of plant operation. Since the ODCM does not affect accidents previously evaluated in the SAR, these changes will not increase the probability of these evaluated accide'nts.
=t f The consequences of accidents evaluated in the SAR are associated withJa' dose to unrestricted areas as a result of radio 6ctive effluents. The ODCM provides the monitoring and calculation requirements to assess and ruport dose to unrestricted areas and the general public. Since the ODCM is used to determine the dose related to radioactive effluents from both normal plant operation and during postulated accidents, the ODCM in itself is not capable of increasing accident consequences.
Part Ill: I . There are no credible accidents or equipment IS failure modes associated with these changes to the I ODCM. The editorial and technical changes incorporated by this revision are being made to ensure that dose resulting from radioactive effluents is accurately determined. Calculations and reporting requirements of the ODCM do not create the possibility of an accident, therefore creating an accident of a different type it, also not possible. Equipment operation is not affected by the ODCM, therefore malfunctions of equipment IS of a different type than previously evaluated in the SAR are not possible. (continued) -
CLASS CODE: SNNNI ~ CPS NO.1005. 06F003 -(Rev. 0) LOG - REV. Page 4 of _ 4 __ SAFETY EVALUATION CONTINUATION SifEET i Document Evaluated: OffsitiLDozeIalculation_ Manual (ODCMI Provide the justification / references / explanation for all answers on cover sheet as follows (attach additional sheets, as necessary): Justification (continued): Part IV: The changes incorporated by this revision to the ODCM bring the ODCM into full compliance with the rzquirements of the Technical Specifications for reporting dose to unrestricted areas as a result Of liquid and gaseous effluents. These changes will not reduce the margin of safety defined in the basis for any Technical Specification. Liquid radweste effluents released from CPS will meet 10CFR2O concentration limits at the point of discharge to the unrestricted area. This design and operation object!ve will be achieved at all times. Actual discharges of liquid radweste effluents will normally occur on a batch basis and tt e average concentration at the point of discharge will be only a small percentage of the allowed limits. USAR Section 11.5 provides a description of radiation monitoring, sampling and effluent control systems. Cumulative quarterly dose contributions due to radioactive effluents released to the unrestricted area will be determined once every 31 days. 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 Purge and mechanical vacuum pump discharge may be considered short term releases. There are two gaseous effluent release points to the environment: the Common Station HVAC Stack cod the Standby Gas Treatment System (SGTS) Stack. The SGTS is an Engineered 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 inputs.
1
, CPS No. 1005.06F001 SAFETY EVALUATION SCREENING FORM (8.2.2.a) DOCUMENT EVALUATED: Offsite_ Dose _CalculatiortManuakflevision_15 (8.2.2.b) DESCRIPTION OF CHAFGE: .
Revised Table 1.1 1. Added a footnote to clarify " frequency
- as it applies to composite samples. I Revised Section 2.3.1. The Operational Requirement limitation was revised to match Technical Specification Amendment No. 95, Section 5.5.4.b.
Revised Table 2.31, Table Notation "a." Revised the definition for " delta T" to clarify that the elapsed time for plant effluents is the time between the midpoint of sample collection and the " midpoint of the counting interval" in seconds. Revised Section 2.3.5. The Component Cooling Water (CCW) sampling requirement now applies only when the Fuel Fool Heat Exchanger is being supplied by the Shutdown Service Water (SX) System. (continued) (8.2.2.c) AFFECTED SYSTEM (S) / COMPONENT (S) / FUNCTIONS None 10CRF50.59 APPLICABILITY DETERMINATION (8.2.2.1) (Refer to Appendix A for guidance for the following questions) Yes No g Is this a change to the facility as described in the SAR? (That is, is the design, function, or method of performing the function of a structure, system or conponent described by text or drawing in the SAR being changed?] Yea d No _ Is this a change to a procedure as described in the SAR? (That is, is a procedure that is. outlined, summarized or that is conpletely described in the SAR being changed?) Yos _ No f Is this a test or experiment not described in the SAR7 (That is, is a test or experiment being conducted which might affect safe operation of the plant which was not anticipated in the SAR7) Yes No f Does this change require a change to the CPS Tech Specs? If yes, process the change in accordance with CPS No. 1038.01. ORM Impact (8.2.2.2) (Refer to Appendix B for guidance for the following question) Yea _ No f Is this a change (other than an editorial change) to the Operational Requirements Manual? If yes, couplete a safety evaluation and process the change in accordance with CPS No. 1038.03. IMPACT ON OTHER LICENSING BASIS DOCUMENTS (8.2.2.3) (Refer to Appendix B for guidance for the following question) Yas d No _ Does this change directly affect any of the following programs: Technica) Specification Bases Physical Security Plan Emergency Plan OA Program Description Licensed OperatoE Requalification Program Offsite Dose Calculation Manual - Process Control Program Fire Protection Plan Enviromental Protection Plan Rev. No. 3_ Page No. 2 of 3 (
l CPS No. 1005.06F001 DOCUMENT EVALUATED: ___ Of f site _ Dose _CalculationfAanuaLJievision_15_ i i JUSTIFICATION FOR "YES/NO" ANSWERS: (0.2.2.1.2, 8.2.2.3) I Description (continued): I Add:d new Section 2.3.6. This section incorporates corrective action CR 1-96-10 260. R:vis:d Table 2.7-1. Added new item 2.d for the CCW PRM. This change is being made as a result of corr:ctive action CR 1-96 10 260. Revis:d Table 2.7-1, Remedial Requirement 2.a. Added a clarifying statement to specify which equipment is required to be operable. , 1 Revis:d Table 2.7-2. Added new item 2.d fo the CCW PRM. This change is being made as a result of c:rr:ctive action CR 1-96-10-260. Revised Surveillance Requirement (SR) 3.4.1.1. This SR cross-references the wrong ODCM Section. Noble g:s dose rate calculations are performed in accordance with Section 3.4.2, not Section 3.4.3. This was a typographical error introduced by a previous ODCM revision. Revised Surveillance Requirement (SR) 3.4.1.2. This SR cross-references the wrong ODCM Section. Radi: iodines, particulates and tritium dose rate calculations are performed in accordance with Section 3.4.3, not Section 3.4.4. Section 3.4.4 no longer exists. This was a typographical error introduced by a previous ODCM revision. Revised Table 3.4-1. Deleted Table Notation "2" from items A.2 and A.3 " Sampling Frequency" and item B.1 3
' Analysis Frequency." These were typographical errors introduced when the table was reformatted by a j previous ODCM revision. i Revised Table 3.4-1, Table Notation "a." Revised the definition for " delta T" to clarify that the elapsed time for plant effluents is the time betwaen the midpoint of sample collection and the " midpoint of the counting ;
int:rval" in seconds. { (continued)
}
1
REFERENCES:
(0.2.2.1.2) I Offsite Dose Calculation Manual (ODCM): Table 1.1-1,1.2.2.8.3, 2.3.1, Table 2.3-1, 2.3.5, 2.3.6, f Tcble 2.71, Table 2.7-2, SR 3.4.1.1, SR 3.4.1.2, Table 3.4-1, 3.4.2, 3.4.3, Table 3.9.1-2, Table 3.9.2-1, 5.1, Tcble 5.1-1, 5.2, 9.2.6.1, 9.2.9.1, 9.2.9.2, 9.2.11, 9.2.11.1 ) USAR Sections: 1.8, Table 11.5-1. Table 11.5-2, Table 15.2.4-3a Technical Specifications: 5.5.1, 5.5.4, 5.5.4.b, 5.6.2, 5.6.3 Oper:tional Requirements Manual (ORM): 6.8.4.c Regulatory Guides: 1.21, 1.109, 1.111 - Code cf Federal Regulations (CFR): 10CFR20.1302 10CFR20, Appendix B, Table 2, Column 2; 10CFR50.36a; 10CFR50 Appendix A: 10CFR50 Appendix 1: 40CFR190 l CR 196-10-260; SER Amendment No. 95; CPS No. 3212.01 Prcpared by: ' b.3 . Loy<_, A Date: Mn l (0.2.3) Printed Name Signature l Review:d by: W._ Scott _Klein
- Date: 7 ZI'97 (8.2.4) Printed Name Signature Rev. No. 3 Page No. 3 of 3
)
CLASS CODii: SNNNI CPS No.1005.06F003 (Rev.0) LOG __- REV. _ _ Page _1_ of __8_ SAFETY EVALUATION CONTINUATION SHEET Document Evaluated: Offsite_DoseIalculationManuaLBevision_15 Provide the justification / references / explanation for all answers on cover sheet as follows (attach additional sheets, as necessary): Description (continued): Revised Table 3.4-1 Table Notation 4. Added "on the applicable PRM (HVAC or SGTS)." This notetion only applies to HVAC and SGTS noble gas monitors, not to the Off-Gas noble gas monitor. Revised Table 3.9.1-2 headings. Revised Table 3.9.2-1. This change moves the Effluent System Flow Rate Measuring Devices from HVAC and SGTS PRMs to new Table Steps 3 and 4. Added alternate flow rate measuring devices OFIVG004 and OFIVG104 to SGTS, Table Step 4. Revised Table 3.9.2-1, Remedial Requirement 8.a. Added a clarifying statement to specify which equipment is required to be operable. Revised Section 5.1, Remedial Requirement "c." The correct report associated with Technical Specification 5.6.2 is the
- Radiological Environmental Operating Report."
Revised Table 5.1-1, Table Notation "a." The correct report associated with Technical Specification 5.6.2 is the " Radiological Environmental Operating Report." Revised Section 5.2, Remedial Requirement "a." The correct report associated with Technical Specification 5.6.2 is the " Radiological Environmental Operating Report." Revised Gection 9.2.6.1. Added a description for the "X" variable for this equation. Revised Sections 9.2.9.1 and 9.2.9.2. Added " meters" to the "X" variable column heading. Revised Section 9.2.11.1. This step contained an error associated with the plume elevation. In accordance with the section heading 9.2.11, this equation applies to " elevated" level, not ground level. Justification: This revision to the ODCM contains the following EDITORIAL changes:
- 1) Revised Table 2.3-1, Table Notation "a" to clarify the definition for elapsed time (delta T) for the radioactive decay factor used in the LLD calculation. For plant effluents, the elapsed time is the time between the midpoint of sample collection and the midpoint of the counting interval, in seconds. This change removes the ambiguity from the previous version of the definition and aligns the definition with the controlled computer software used for calculating the LLD. .
- 2) Revised Surveillance Requirements (SR) 3.4.1.1 and 3.4.1.2. These SRs cross-referenced the wrong dose rate calculation sections. SR 3.4.1.1 should reference Section 3.4.2 and SR 3.4.1.2 should reference Section 3.4.3. These errors were introduced by a previous revision to the ODCM.
- 3) Revised Table 3.4-1. Deleted Table Notation "2" from items A.2 and A. 3 " Sampling Frequency" and l Item B.1 " Analysis Frequency." These were typographical errors introduced when the table was l reformatted by a previous ODCM revision. These changes are consistent with the sampling and analysis requirements found in USAR Section 1.8. -
1 I (continued) j 1 i
. _ _ _ _ _ _ _ _ _ _ ____________._-________________-____-_-o
CLASS CODE: SNNNI CPS No.1005.06F003 (Rev.0) LOG . _ REV.___ Page _ l _ of J_ SAFETY EVALUATION CONTINUATION SHEET - Document Evaluated: 0.ffsite_ Dose _ Calculation _ManuaLilevlalon 15 Provide the justification / references / explanation for all answers on cover sheet as follows (attach additional sheets, as necessary): Justification (continued):
- 4) Revised Table 3.4-1, Table Notation "a" to clarify the definition for elapsed time (delta T) for the rtdioactive decay factor used in the LLD calculation. For plant effluents, the elapsed time is the time between the midpoint of sample collection and the midpoint of the counting interval, in seconds. This change removes the ambiguity from the previous version of the definition and aligns the definition with the controlled computer software used for calculating the LLD.
- 5) Revised Table 3.41, Table Notation "4" to clarify which noble gas monitors apply to this note. Added a statement *on the applicable PRM (HVAC or SGTS)" to prevent confusing this requirement with the Offgas noble gas monitors. This revision clarifies the applicability for the noble gas monitors. in accordance with Table 3.4-1, the listed gaseous release types are the Station HVAC Exhaust and the Standby Gas Treatment System Exhaust (when flow exists).
- 6) Revised Table 3.9.1-2 table headings. These headings were misaligned by a previous revision. This is a typographical error.
- 7) R; vised Section 5.1, Remedial Requirement "c." The correct report associated with Technical Specification 5.6.2 is the " Radiological Environmental Operating Report." This is an editorial change to clign the ODCM with Technical Specifications.
- 8) Revised Table 5.1-1, Table Notation "a." The correct report associated with Technical Specification 5.6.2 is the " Radiological Environmental Operating Report." This is an editorial change to align the ODCM with Technical Specifications.
- 9) Revised Section 5.2, Remedial Requirement "a." The correct report associated with Technical j Specification 5.6.2 is the " Radiological Environmental Operating Report." This is an editorial change to r.lign the ODCM with Technical Specifications.
- 10) Revised Section 9.2.6.1. Added a description for the "X" variable for this equation. The calculation ,
- has not been revised, therefore this is an editorial change.
- 11) Revised Sections 9.2.9.1 and 9.2.9.2. Added " meters" to the "X" variable column heading. This is an editorial change.
- 12) Revised Section 9.2.11.1. This step contained a typographical error associated with the plume clevation. In accordance with the section heading 9.2.* ? 'his equation applies to " elevated" level, not ground level.
(csntinued) a
I t CLASS CODE: SNNNI CPS No.1005.06F003 l (Rev.0) LOG ___ REV._ , Page _3_ of __8__ l l SAFETY EVALUATION CONTINUATION SIIEET Document Evaluated: Offsite_ Dose _Calculaticaldanuakflevision_15 Provide the justification / references / explanation for all answers on cover sheet as follows (attach additional sheets, as necessary): Justification (continued): The editorial changes incorporated by this revision do not change the intent of the ODCM and are consistent with the regulatory requirements of 10CFR20.1302,10CFR50.36a,10CFR50 Appendix 1,40CFR190. These changes maintain the levels of radioactive effluent control required by these regulations and do not tdversely impact the reliability of effluent, dose, or setpoint calculations. This revision to the ODCM contains the following TECHNICAL. changes:
- 1) Revised Table 1.1-1 to add a clarifying footnote for composite samples. The composite sampling-frequency applies to the time period over which the sample is composited (duration of the composite). l To be representative of the average quantities and concentrations of radioactive materials released in liquid cnd in particulate form in gaseous effluents, samples for compositing are collected in proportion to the rate cf flow of the effluent stream or in propoltion to the volume of each batch of effluent releases. Prior to analysis of liquid samples, the composite is thoroughly mixed so that the sample is representative of the average effluent release.
Periods of collection for composites should be as short as practicable to preclude the loss of radioactive material by deposition on walls of the sample container or volatilization of potentially volatile material. This revision does not change the basis for composite samples. Composite samples are either grab samples collected at different times from the same sample point or are continuous samples. The composite samples cre collected over a finite period of time, not instantaneously. This methodology ensures that the effects of variable or irregular discharges and operations are monitored during the entire period during which discharges occur.
- 2) Revised Section 2.3.1 to change the limit for liquid radioactive material released to unrestricted areas in cccordance with Technical Specification Licensing Amendment No. 95, Section 5.5.4.b. The current Technical Specifications allow the concentration of radioactive materials released in liquid effluents to .
f UNRESTRICTED AREAS to be limited to " ten times" the concentrations specified in 10CFR20, Appendix B, . Table 2, Column 2 for nuclides other than dissolved or entralned noble gases. This revision to the ODCM } i cligns Section 2.3.1 to the current Technical Specifications and dr'es not change the current Technical Specifications or 10CFR20, Appendix B, Table 2, Column 2. In accordance with Technical Specification 5.5.4, the Radioactive Effluent Controls Program " conforms to 10CFR50.36a for the control of radioactive effluents and for maintaining the doses to members of the public j from radioactive effluents as low as reasonably achievable. The program shall be contained in the ODCM, shall be implemented by procedures, and shall include remedial actions to be taken whenever the (continued)
CLASS CODE: SNNNI CPS No.1005.06F003 (Rev.0) LOG _- _ REV.__ Page _4_ of __s_ SAFETY EVALUATION CONTINUATION SHEET Document Evaluated: Offaite. Dose _CalculationRanuaLBevision 15 4 Provide the justification / references / explanation for all answers on cover sheet as follows (attach additional sheets, as necessary)* i i Justification (continued): program limits are exceeded. The program shallinclude ' Limitations on the concentrations of radioactive matuial released in liquid effluents to unrestricted areas, conforming to ten times the concentration values in 10CFR20, Appendix B, Table 2, Column 2.'" This tsvision aligns the ODCM with Technical Specifications 5.5.4.b.
- 3) Revised Section 2.3.5 to eliminate unnecessary weekly sampling of the CCW system while still providing I cs:ur:nces that radioactive materials are not being released to the Ultimate Heat Sink (UHS) via CCW. This ch:nge will require CCW to be sampled prior to placing the Fuel Pool Heat Exchanger in the Shutdovsn Service Water (SX) cooling mode, then weekly thereafter while in this mode. This change also corrects a misnomer which described the potential release of CCW radioactivity to the UHS as a " batch" release.
The fuel pool cooling and cleanup (FPC&C) system maintains the water temperature, purity, and radiation 1;vilin the spent fuel and upper containment pools within acceptable limits. This system has two 100Wcapacity processing trains with each consisting of a transfer pump, filter domineralizer unit, and heat cxchanger. Each heat exchanger is designed to provide the required cooling capacity to accommodate ! cxpected long term spent fuel storage. Both processing trains may be operated in parallel for cooling larger thin cxpected heat loads. The RHR system is connected to the FPC&C system to provide supplemental cooling during shutdown, if necessary. A filter-demineralizer unit is employed to rnaintain water purity and contr:I radioactive exposure. The CCW system, (which is the normal source of FPC&C heat exchanger cooling) is a closed loop so that continued radioactive leakage will increase the CCW system radioactivity concentration but no discharge to tha environment will occur. Radiation monitors are provided downstream of each fuel pool heat exchanger cnd cn the service water effluent. A process radiation monitoring channel monitors for leakage into each cooling water header downstream of the RHR heat exchangers and on the common header downstream of thi RWCU non-regenerative heat exchangers. Each channel will alarm on high radiation conditions indicating proc:ss leakage into the cooling water. No isolation trip functions are performed by these monitors. - If the fuel pool water temperature rises above 120'F, the FPC&C heat exchanger cooling media may be trcnsfrrred by the operator from the component cooling water (CCW) system to the shutdown service water (SX) system. The design inlet water temperature of the CCW system is 105*F, while the SX design inlet t:mperature is 95'F. This change in cooling media increases the heat dissipation capability of the one FPC&C train. If necessary, the Shutdown Service Water (SX) System can also provide cooling of the FPC&C hut exchangers and pump motors under loss of offsite power conditions. i - (centinued) -
)
CLASS CODE: SNNNI CPS No.1005.06F003 (Rev. 0) LOG _. ._ - REV. _ Page _S._. of _A SAFETY EVALUATION CONTINUATION SIIEET Document Evaluated: Offsiin_ Dose calculation ManuaLBevision 15 Provide the justification / references / explanation for all answers on cover sheet as follows (attach additional sheets, as necessary): Justification (continued): Transfer nf secondary cooling water is by operator action. In the event of leakage across the heat cxchangers, the potential exists for radioactive materials to be present in the CCW system. The two potential paths for radioactive inleakage to the SX are the RHR heet exchangers and the fuel pool cooling and cleanup (FPC&C) heat exchangers. The SX operates at a higher pressure than the FPC&C, therefore, the probability l of rariioactive material leakage from the FPC&C system is minimized. Radiation monitors are located in the service water discharge from the RHR and FPC&C heat exchangers. If a high radiation alarm from the heat ! cxchangers occurs, the operator can isolate the heat exchanger by closing motor-operated isolation valves in the service water inlet and discharge. If this action is deemed necessary, the second RHR or FPC&C heat cxchanger can then be placed into operation. The process radiation monitoring system, of which the'se monitors are part, will help to assure that any radioactivity released to the Ultimate Heat Sink (UHS) will not cxceed allowable limits if the SX system is providing the FPC&C heat exchanger service water and leakage occurs, the radioactivity will be diluted by the SX system and discharged to the UHS. Operator action would j be required to correct the condition. Current ODCM sampling and analysis requirements for the CCW system specify a weekly surveillance. 'The intent of this sampling requirement is to ensure that potential releases to the Ultimate Heat Sink via the SX system are monitored. This revision provides adequate controls to obtain CCW samples prior to enterin0 the SX cooling mode. l
- 4) Added new Section 2.3.6 to include the CCW PRM setpoints in the ODCM due to the CCW system operating at a higher pressure than the Plant Service Water (WS) system at the heat exchangers. This cperating condition provides a potential pathway for radioactive materials to enter the WS system. This change assures that a potentially unmonitored release path does not exist.
l This change implements a corrective action from Condition Report (CR) 1-96-10-260. CR 196-10-260 has identified a discrepancy regarding Plant Serv:ce Water (WS) system pressure and CCW system pressure. Depending on WS load and number of WS pumps operating, CCW pressure could possibly be higher than WS pressure. A Safety Evaluation (Log 97-062) determined that this was not an unreviewed safety , question. This revision incorporates the CCW PRM setpoint surveillance requirements into the liquid effluent monitoring program to ensure compliance with 10CFR20 release rate limits.
- f. continued)
CLASS CODE: SNNNI CPS No.1005.06F003 (Rev.' 0) LOG __ _ _REV. Page _6_ of a _ SAFETY EVALUATION CONTINUATION SHEET Document Evaluated: Offsite_Dase_ Calculation Manuaulevision_15 Provide the justification / references / explanation for all answers on cover sheet as follows (attach additional sheets, as necessary): Justification (continued):
- 5) Rsvised Table 2.71 to include the CCW PRM monitoring instrumentati e ODCM due to the CCW syst:m operating at a higher pressure than the Plant Service Water (WS. t the heat exchangers.
This operating condition provides a potential pathway for radioactive mate nter the WS system. This chang 2 assures that a potentially unmonitored release path does not exist. This change implements a corrective action from Condition Report (CR) 196-10-260. CR 1-96-10-260 has identified a discrepancy regarding Plant Service Water (WS) system pressure and CCW system pressure. Depending on WS load and number of WS pumps operating, CCW pressure could possibly be higher than WS pressure. A Safety Evaluation (Log 97-062) determined that this was not an unreviewed safety question. This r; vision incorporates the CCW PRM monitoring instrumentation requirements into the liquid effluent progrzm to ensure compliance with 10CFR2O release rate limits. The minimum channels operable and rImidial requirements for the CCW PRM are included in this table.
- 6) Revised Table 2.7-1 Remedial Requirement 2 to add a clarifying statement for instrument availability, in ordIr to be considered operable, both the communication link and MCR-CCT are required to be operable, This change is consistent with Table 2.7-1 Table Notation "(a)" and Table 2.7-2, Table Notation "5."
This ravision ensures that the liquid effluent monitoring instrumentation provides the capability of the MCR Central Control Terminal (MCR-CCT) to provide the alarm status of the applicable radiation monitor channels. I
- 7) Revised Table 2.7-2 to include CCW PRM surveillance requirements in the ODCM due to the CCW system i operating at a higher pretsure than the Plant Service Water (WS) system at the heat exchangers. This ,
operating condition provides a potential pathway for radioactive materials to enter the WS system. This ! change assures that a potentially unmonitored release path does not exist. - (continued)
- 4 4
CLASS CODE: SNNNI CPS No.1005.06F003 (Rev.0) LOG _ ___ REV.____ Page _7_ of 8_ SAFETY EVALUATION CONTINUATION SHEET Document Evaluated: Offsite Dose CalculationAlanual. Revision 15 Provide the justification / references / explanation for all answers on cover sheet as follows (attach additional sheets, as necessary): Justification (continued): This change implements a corrective action from Condition Report (CR) 196-10-260. CR 196-10-260 has identified a discrepancy regarding Plant Service Water (WS) system pressure and CCW system pressure. Depending on WS load and number of WS pumps operating, CCW pressure could possibly be higher than WS pressure. A Safety Evaluation (Log 97-062) determined that this was not an unreviewed safety question. This revision incorporates the CCW PRM monitoring instrumentation surveillance requirements into the liquid cffluent program to ensure compliance with 10CFR20 release rate limits. The channel check, source check, channel calibration, and channel functional test requirements for the CCW PRM are included in this table.
- 8) Revised Table 3.9.2-1. The Effluent System Flow-Rate Measuring devices listed in Table Steps 1.f and 2.f are not a part of the associated HVAC or SGTS PRMs as indicated. These devices are being moved to their own separate instrument sections 3 and 4 (respectively) to avoid confusion. This is an editorial change since all related minimum channels operable, applicability, and remedial requirement information still applies and is not being changed. This revision adds two alternate SGTS flow-rate measuring devices, OFIVG004 cnd OFIVG104, to the SGTS Effluent System Flow-Rate Measuring Device " Instrument" section. Thes'e' alterna".e devices also meet the minimum channels operable, applicability, and remedial requirements for this instrument.
Revised Table 3.9.2-1 Remedial Requirement "8a" to add a clarifying statement for instrument availability. In crder to be considered operable, both the communication link and MCR-CCT are required to be operable. This change is consistent with Table 2.7-1 Table Notation "(al" and Table 3.9.1-2, Table Notation "3." This revision ensures that the offgas radiation monitoring instrumentation provides the capability of the MCR Central Control Terminal (MCR-CCT) to provide the alarm status of the applicable radiation monitor channels. The purpose of the Offsite Dose Calculation Manual (ODCM) is to provide the methodologies and parameters used for assuring compliance with the radiological effluent dose limitations provided by iOCFR20,10CFR50 Appendix A,10CFR50 Appendix 1, and 40CFR190. The ODCM contains information necessary to calculate effsite doses resulting from radioactive liquid and gaseous effluents, calculations for gaseous and liquid . cffluent monitoring alarm and trip setpoints, and the elements needed to conduct the radiological cnvironmental monitoring program. The radioactive effluent controls program and the radiological environmental monitoring program are described. (continued)
CLASS CODE: SNNNI CPS No.-' 1005.06F003 (Rev.0) LOG _._ ___ REV._ Page _8_ of .d_ SAFETY EVALUATION CONTINUATION SHEET Document Evaluated: Offsite_ Dose _CalculationJeanuaLBevision_15 Provide the justification / references / explanation for all answers on cover sheet as follows (attach additional sheets, as necessary): Justification (continued): The editorial changes incorporated by this revision to the ODCM do not modify calculations for dose or alarm setpoints. The editorial changes incorporated by this revision align the ODCM with Technical Specification reporting requirements, clarify notes, clarify and reorganize tables, add descriptions for calculation variables, cnd carrect ob'vious typographical errors. The trchnical changes incorporated by this revision align the ODCM with Technical Specification 5.6.4.b liquid release limits, eliminate unnecessary sampling for the CCW when shutdown service water (SX) is not cupplying cooling water to the fuel pool heat exchan'gers, add CCW PRMs to the monitoring programf specify that the communication links are included in PRM channel check operability, and add alternate flow rate measuring devices for the SGTS gaseous effluent monitoring instruments. These technical changes are consistent with the requirements of 10CFR20,10CFR60 Appendix A,10CFR50 Appendix 1, and 40CFR190. Calculations for dose and alarm setpoints are not modified by these technical changes. This revision to the ODCM does not affect structures, systems or components. The changes being - incorporated by this revision are administrative in nature. These changes will ensure that dose from radioactive effluents is monitored and reported in accordance with the requirements of Technical Specifications,10CFR20,10CFR50, and 40CFR190. Since the design, function, or method of performing the function of SSC is not changed by this revision, this is not a change to the facility as described in the SAR. The ODCM implements the requirements of Technical Specifications,10CFR20,10CFR50, and 40CFR190. Since ODCM activities are included by reference and description in the Technical Specifications, this revision is considered a change to procedures as described in the SAR. Performing radioactive effluent surveilla: ces and dose calculations are routine parts of the overall effluent monit: ring program. The ODCM incorporates the programs and procedures necessary to ensure that survziliances are performed when required and that their completion is adequately documented. Actions to notify plant management are also provided when surveillances do not meet the specified acceptance criteria. , This change does not affect the operad.m of plant equipment or the ability to monitor radioactive effluents gnd thIir associated dose, therefore this revision does not constitute a test or experiment not described in ths SAR. BecIuse these changes affect only monitoring and surveillance activities associated with the ODCM, there cre no changes needed to Technical Specifications, Tech Spec Bases, or the ORM. Th3 ODCM changes are not contrary to Technical Specifications, Tech Spec Bases, ORM, Environmental Plan, Security Plan, Emergency Plan, QA Program Description, Seismic Qualification, t.icensed Operator f l Requilification Program, Radiological Controls, Process Control Program, Accident Analysis, or Fire Pr:tection Program. No changes are required to these programs as a result of the ODCM program revision.
CPS NO. 1005.06F002 Page 2 of (8.3.1.1.a) LOG - REV. DOCUMENT EVALUATED: Offsite Dose Calculation Manual (ODCMI REVISION: 1 !i __ TITLE: Offsite Dose Calculation Manual (ODCMI Change UNREVIEWED SAFETY QUESTION DETERMINATION (8.3.1.1.e) (Attach justification for following questions on CPS No. 1005.06F003) Part I -- Impact on equipment malfunctions evaluated as the design bases Yes _ No g 1. Will change increase the probability of a malfunction of equipment important to safety evaluated previously in the SAR? Yes No J 2. Will change increase the consequences of a malfunction of equipment important to safety evaluated previously in the SAR? Part II -- Impact on accidents evaluated as the design bases Yes No ) 3. Will change increase the Isrobability of an accident previously evaluated in the SAR? Yes No j 4. Will change increase the consequences of an accident previously evaluated in the SAR? Part III -- Potential for creating a new type of accident or equipment malfunction Yes No 1 5. Will change create the possibility of an accident of a different type than any evaluated previously in the SAR? Yes No 1 6. Will change create the possibility of a malfunction of equipment important to safety of a different type than previously evaluated in the SAR? Part IV -- Impact on the Margin of safety Yes No1 ~7. Will change reduce the Margin of Safety as defined in the basis for any technical specification? , l suum ar (8.3.1.1.f, 8.3.1.1.g)
/ Change is safe, no USQ exists, and requires no change to technical specifications. The change may be implemented upon FRG review.
1 Change is safe, however there is an USQ, or requires a change to technical specifications. The change requires NRC approval prlor to implementation. 1 R2v. No. I
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CPS-ODCM G. O a6 4 l ILLINOIS POWER COMPANY . CLINTON POWER STATION : UNIT 1 OFFSITE DOSE CALCULATION MANUAL Docket No. 50-461
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1 FRG" bA /
/ 7-IP17 Date Manager Cli6to W wer Station i 7/rs/9;7 tate'~
155- % -010 1 CLINTON-1 Rev.15-7/97 j
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CPS-ODCM Illinois Power Company Clinton Power Station OFFSITE DOSE CALCULATION MANUAL Table of Contents Section Title Page 1.0 PREEACE 1-1 1.1 Definitions 1-1 1.2 General Operation Requirements 1-4 1.3 General Surveillance Requirements 1-4 1.4 Effluent Concentration Limit (lim) 1-6 Calculation Requirements 2.0 LIQUID EFFLUENTS 2.1 Introduction 2-1 1 2.2 Liquid Radwaste Discharge Process 2-1 Radiation Monitoring (PRM) System I 2.3 10CFR20 Release Rate Limits 2-1 2.3.1 Liquid Effluent Concentration - 2-2 Operation and Surveillance Requirements 2.3.2 Liquid Radwaste Discharge PRM 2-6 Setpoints . i 2.3.3 Plant Service Water Effluent 2-11 PRM Setpoints 2.3.4 Shutdown Service Water (SX) 2 Effluent PRM Setpoints 2.3.5 Fuel Pool Heat Exchanger Service 2-12 Water Effluent PRM Setpoints 2.3.6 Component Cooling Water PRM 2-12 Setpoints l CLINTON-1 i s Rev.15-7/97
CPS-ODCM Illinois Power Company Clinton Power Station l
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OFFSITE DOSE CALCULATION MANUAL j Table of Contents Section Title Page I 2.0 2.4 10CER50, Appendix I Release Rate Limits 2-13 2.4.1 10CFR50, Appendix I Release Rate 2-13 Limits - Operation and Surveillance Requirements 2.4.2 Discussion 2-14 2.5 Liquid Radwaste Treatment System - 2-24 2.5.1 Liquid Radwaste Treatment System - Operation and 2-24 l Surveillance Requirements 2.5.2 Temporary Liquid Radwaste 2-25 l Hold-up Tanks f i 2.6 Doses From Other Significant Liquid Effluent Pathways 2-25 2.7 Radioactive Liquid Effluent Monitoring 2-25 Instrumentation 2.7.1 Radioactive Liquid Effluent 2-25 Monitoring Instrumentation-Operation and Surveillance , Requirements 3.0 GASEOUS EFFLUENTS 3-1 3.1 Introduction 3-1 3.2 Gaseous Effluent Release Point Monitoring 3-2 3.2.1 HVAC Stack Process Radiation 3-2 Monitoring (PRM) System 3.2.2 SGTS Stack Process Radiation 3-2 Monitoring (PRM) System CLINTON-1 ii Rev.15-7/97 j
CPS-ODCM Illinois Power Company Clinton Power Station OFFSITE DOSE CALCULATION MANUAL Table of Contents Section Title Page 3.0 3.3 Main Condenser Off-Gas Monitoring System 3-3 3.3.1 Pre-Treatment Air Ejector 3-3 Off-Gas PRM - 3.3.2 Post-Treatment Air Ejector 3-4 Off-Gas PRM 3.4 10CFR20 Release Rate Limits 3-4 3.4.1 10CFR20 Release Rate- Limits - 3-4 Operation and Surveillance Requirements 3.4.2 Dose Rate Due to Noble Gases 3-9 3.4.3 Dose Rate Due to Radioiodines, 3-9 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 - Operations 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 3-25 3.6.1 Gaseous Radwaste (Offgas 3-25 Treatment) System - Opdration and Surveillance Requirements CLINTON-1 lii Rev.15-7/97 e
CPS-ODCM l I Illinois' Power Company Clinton. Power Station OFFSITE DOSE CALCULATION MANUAL l Table of Contents Section -Title Page 3.0 3.7 Ventilation Exhaust. Treatment 3-27 3.7.1 Ventilation Exhaust Treatment 3-27 System - Operation and Surveillance Requirements l 3.8 Effluent Monitor Setpoint Calculations 3-28 3.8.1 Total Body Dose Rate Setpoint 3-28 1 3.8.2 Skin Dose Rate Setpoint 3-30 , 3.9 Radioactive Gaseous Monitoring 3-31 l Instrumentation l l 3.9.1 Offgas Radiation Monitoring 3-31
- Instrumentation - Operation and Surveillance Requirements ln 3.9.2 Radioactive Gaseous Effluent 3-38 Monitoring Instrumentation -
l Operation and Surveillance Requirements 4.0 COMPLIANCE WITH 40CFR190 4-1 4.1 Total Dose - Operation and Surveillance 4-1 l Requirements 4.1.a Special Report Requirements 4-1 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 5-1 l 5.1 Monitoring Program - Operation and 5-1 Surveillance Requirements 5.2 Land Use 'ensus C - Operation and 5-21 Surveillance Requirements CLINTON-1 iv Rev.15-7/97
CPS-ODCM Illinois Power Company Clinton Power Station OFFSITE DOSE CALCULATION MANUAL Table of Contents Section Title Page 5.0 5.3 Interlaboratory Comparison Program 5-22 5.3.1 Interlaboratory Comparison 5-23 Program - Operation and Surveillance Requirements 6.0 BASES FOR OPERATION AND SURVEILLANCE 6-l ' REQUIREMENTS 6.1 General Operation and Surveillance Requirements - 6-1 6.2 Monitoring Instrumentation 6-2 6.3 Radioactive Effluents 6-3 6.3.1 Liqu'id Effluents 6-3 i 6.3.2 Gaseous Effluents 6-5 6.3.3 Total Dose 6-9 6.4 Radiological Environmental Monitoring 6-10 7.0 REPORTING REQUIREMENTS 7-1 7.1 Annual Radiological Environmental 7-1 Operating Report 7.2 Radioactive Effluent Release 7-2 Report 8.0 ADJUSTMENT OF THE CPS ODCM METHODOLOGY 8-1 9.0 ATMOSPHERIC TRANSPORT AND DISPERSION MODEL 9-1 9.1 Introduction 9-1 i CLINTON-1 v t _ev.15-7/97 R_ _
1 l CPS-ODCM Illinois Power Company Clinton Power Station OFFSITE DOSE CALCULATION MANUAL Table of Contents Section Title Page 9.0 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 9-3 Wind Speed 9.2.3 Determination of Release Mode 9-3 and the Entrainment Coefficient 9.2.4 Calculation of Vertical Standard 9-4 Deviation 9.2.5 Calculation of the Building Wake 9-5 Correction 9.2.6 Calculation of Momentum Plume 9-5 Rise 9.2.7 Calculation of Effective Plume 9-6 Height 9.2.8 Determination of Affected 9-7 Sectors 9.2.9 Calculation of Depletion and 9-8 Deposition Factors 9.2.10 Ground Level X/Q, D2DPXQ, D1XQ, 9-12 D/O Analysis 9.2.11 Elevated X/Q, D2DPXQ,.D1XQ, D/O 9-13 Analysis CLINTON-1 _ _ _ _ _ vi Rev.15-7/97 ;
C PS-ODCM Illinois Power Company Clinton Power Station OFFSITE DOSE CALCULATION MANUAL Tables , Table Title Page 1.1-1 Surveillance Frequency Notation 1-6
- 2.3-1 I Radioactive Liquid Waste Sampling and Analysis Program 2-3 2.4-1 l
Adult Ingestion Dose Commitment Factors - A 13 2-16 2.4-2 Bioaccumulation Factors - BFs 2-18 2'.4-3 Adult Ingestion Dose Factors - DF i 2-19 2.7-1 Radioactive Liquid Effluent Monitoring 2-27 Instrumentation 2.7-2 Radioactive Liquid Effluent Monitoring ! 2-30 Instrumentation Surveillance Requirements 3.4-1 Radioactive Program Gaseous Waste Sampling and Analysis 3-6 t 3.4-2 Dose Factors for Noble Gases and Daughters 3-11 3.4-3 Inhalation Pathway Dose Rate Factors (Child) - E ij 3-12 3.4-4 Location of Members of the Public Within the , 3-14 CPS Site Boundary and Their Associated Occupancy Factors 3.9.1-1 Offgas Radiation Monitoring Instrumentation 3-32 3.9.1-2 Offgas Radiation Monitoring Instrumentation 3-36 Surveillance Requirements 3.9.2-1 Radioactive Gaseous Effluent Monitoring 3-39 Instrumentation 3.9.2-2 Radioactive Gaseous Effluent Monitoring - 3-41 Instrumentation Surveillance Requirements 3.5-1 Inhalation Dose Factors for Infant-(DFA ). t 3-45 3.5-2 Inhalation Dose Factors for Child-(DFA ); i 3-47 3.5-3 Inhalation Dose Factors for Teen-(DFA ). t 3-49 CLINTON-1 vil Rev.15-7/97
CPS-ODCM Illinois Power Company Clinton Power Station OFFSITE DOSE CALCULATION MANUAL Tables Table Title Page 3.5-4 Inhalation Dose Factors for Adult-(DFA ). i 3-51 3.5-5 Ground Plane Dose Factors-DFG i 3-53 3.5-6 Ingestion Dose Factors for Infant-(DFL ). i 3-55 3.5-7 Ingestion Dose Factors for Child-(DFL ). i 3-57 3.5-8 Ingestion Dose Factors for Teen-(DFL i). 3-59 3.5-9 Ingestion Dose Factors for Adult-(DFL i). 3-61 3.5-10 Input Parameters for Calculating R.i3 3-63 3.5-11 Input Parameters for Calculating R".13 3-64 3.5-12 Input Parameters for Calculating R*.i3 3-65 3.5-13 Inhalation Pathway Factors - R.13 I (INFANT) 3-66 3.5-14 Inhalation Pathway Factors - R*.13 (CHILD) 3-68 3.5-15 Inhalation Pathway Factors - R*.13 (TEEN) 3-70 3.5-16 Inhalation Pathway Factors - R*.13 (ADULT) 3-72 3.5-17 Cow Milk Pathway Factors - R.13 (INFANT) , 3-74 3.5-18 Cow Milk Pathway Factors - R*.13 (CHILD) 3-76 3.5-19 Cow Milk Pathway Factors - R*.13 (TEEN) 3-78 3.5-20 Cow Milk Pathway Factors - R.33 (ADULT) 3-80 3.5-21 Goat Milk Pathway Factors - R*23 (INFANT) 3-82 3.5-22 Goat Milk Pathway Factors - R*.13 (CHILD) 3-84 3.5-23 Goat Milk Pathway Factors - R*.13 (TEEN) 3-86 c 3.5-24 Goat Milk Pathway Factors - R.3 (ADULT) 3-88 ! l 3.5-25 Meat Pathway Factors - R".13 (CHILD) 3-90 3.5-26 Meat Pathway Factors - R".33 (TEEN) 3-92 3.5-27 Meat Pathway Factors - R".i3 (ADULT) 3-94 CLINTON-1 viii Rev.15-7/97
]
i CPS-ODCM i Illinois Power Company 1 Clinton Power Station OFFSITE DOSE CALCULATION MAhTAL Tables Table Title Page 3.5-28 Vegetation Pathway Factors - R*.33 (CHILD) 3-96 3.5-29 Vegetation Pathway Factors - R V.i3 (TEEN) 3-98 3.5-30 Vegetation Pathway Factors - R*.33 (ADULT) 3-100 i 3.5-31 Ground Plane Pathway Factors - R i 3-102 5.1-1 Radiological Environmental Monitoring Program - 5-4 5.1-2 Reporting Levels for Radioactivity 5-17 Concentrations in Environmental Samples. 5.1-3 Detection Capabilities for Environmental Sample 5-18 Analysis Lower Limit of Detection 9.2-1 Gaseous Effluent Release Point Characteristics 9-15 CLINTON-1 ix Rev.15-7/97 _ _ _ _ _ _
CPS-ODCM Illinois Power Company Clinton Power Station l OFFSITE DOSE CALCULATION MANUAL Figures j Figure Title Page 2.1-1 Unrestricted Area Boundary for Liquid Effluents 2-10 )
)
2.5-1 Liquid Radwaste Treatment System 2-21 2.5-2 Shutdown and Fuel Pool Heat Exchanger Service 2-22 Water Effluent Monitors ) I 2.5-3 Solid Radwaste System Simplified Flow Diagram 2-23 3.1-1 CPS Site Boundary For Gaseous Effluents 3-43 3.3-1 Main Condenser Off-Gas Treatment System 3-44 5.0-1 REMP Locations Within 1 Mile of CPS 5 1 5.0-2 'IU2(P Location 1-2 Miles From CPS 5-25 5.0-3 REMP Location 2-5 Miles From CPS 5-26 5.0-4 REMP Locations Greater than 5 Miles From CPS 5-27 ) l l 1 CLINTON-1 x Rev.15-7/97
CPS-ODCM 1.0 GENERAL INFORMATION PREFACE The Clinton Power Station OFFSITE DOFE CALCULATION MANUAL (CPS-ODCM) provides.the methodologies and parameters to be used by Illinois Power Company (.'PC) to assure compliance with the radioactive effluent dose limitations stated in 10CFR20, 10CFR50 Appendix A '(General Design Criteria 60 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 (Draft 7, SPECIFICATIONS FOR BOILING WATER REACTORS to Revision 3). This manual along with station procedures will be used by CPS personnel to demonstrate compliance with the above referenced Federal Regulations. Changes to the CPS-ODCM shall be provided in the l RADIOACTIVE EFFLUENT RELEASE REPORT. l 1.1 Definitions I The following terms are defined so that uniform interpretation of requirements of this manual may be achieved. The defined terms appear in capitalized type l and shall be applicable throughout this manual. CHANNEL CALIBRATION l 1.1.1 ' A CHANNEL CALIBRATION shall be the adjustment, as necessary, of the channel output such that it responds with the necessary range and accuracy to known values of l the parameter that the channel monitors. The CHANNEL CALIBRATION shall encompass the entire channel, including the required sensor, alarm, display, and trip functions, and shall include the CHANNEL FUNCTIONAL TEST. Calibration of instrument channels with resistance temperature detector (RTD) or thermocouple sensors may consist of an in place qualitative assessment of sensor behavior and normal calibration of the remaining adjustable devices in the channel. The CHANNEL CALIBRATION may be performed by means of any series of sequential, overlapping or total channel st.sps so that the entire channel is calibrated. CLINTON-1 1-1 e - __. Rev .15-7 / 97
Ct. ODCM CHANNEL CHECK
-1.1.2 A CHANNEL CHECK shall be the qualitative assessment of channel behavior during operating by observation. This determination shall include, where possible, comparison of the channel indication and/or status with other indications and/or status derived from independent instrument channels measuring the same parameter.
CHANNEL FUNCTIONAL TEST 1.1.3 A CHANNEL FUNCTIONAL TEST shall be the injection of a simulated, or actual, signal into the channel as close to the sensor as practicable to verify OPERABILITY, including required alarm, interlock, display, and trip l functions, and channel failure trips. The CHANNEL
- FUNCTIONAL TEST may be performed by means of any series l of sequential, overlapping or total channel steps so that the entire channel is tested.
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- FREQUENCY NOTATION ;
l 1.1.4 The FREQUENCY NOTATION specified for the performance of I surveillahce requirements shall correspond to the l intervals defined in Table 1.1-1. GASEOUS RADWASTE TREATMENT SYSTEM iI l 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 system and providing for delay or holdup for the purpose of reducing the total radioactivity prior to release to the environment. MEMBER (S) OF THE PUBLIC l 1.1.6 An individual in a controlled or unrestricted area. i However, an individual is not a member of the public i
- during any period in which the individual receives an ;
l occupational dose. ; l 1.1.6a MODE l A MODE shall correspond to any one inclusive combination i of mode switch position, average reactor co,olant temperature, and reactor vessel head bolt tensioning specified in Technical Specification Table 1.1-1 with fuel in the reactor vessel. CLINTON-1 1-2 Rev.15-7/97 ;
CPS-ODCM OPERABLE - OPERABILITY 1.1.7 A system, subsystem, division, component or device shall be OPERABLE or have OPERABILITY when it is capable of performing its specified safety function (s) and when all necessary attendant instrumentation, controls, normal or emergency electrical power, cooling or seal water, lubrication or other auxiliary equipment that are required for the system, subsystem, division, component or device to perform its specified safety function (s) are also capable of performing their related support function (s). REMEDIAL REQUIREMENT
1.1.8 REMEDIP
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
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1.1.11 I An UNRESTRICTED AREA means an area, access to which is neither limited nor controlled by the licensee. VENTILATION EXHAUST TREATMENT SYSTEM 1.1.12 A VENTILATION EXHAUST TREATMENT SYSTEM is any system designed and installed to reduce gaseous radioiodine or radioactive material in particulate form in effluents by passing ventilation or vent exhaust gases through charcoal adsorbers and/or HEPA filters for the purpose of removing iodines or particulates from the gaseous exhaust stream prior to the release to the environment. Such a system is not considered to have any effectfon noble gas effluents. Engineered Safety Festure (ESP) atmospheric cleanup systems are not considered to be VENTILATION EXHAUST TREATMENT SYSTEM components. l l CLINTON-1 1-3 L Rev.15-7/97 _ __ _
CPS-ODCM j l 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) 1.2 General Operation Requirements 1.2.1 Operation Requirements shall be met during the conditions specified therein; except as provided in Operation Requirement 1.2.2.
1.2.2 Upon discovery of a failure to meet an Operation Requirement, the REMEDIAL REQUIREMENT (s) shall be met, except as provided in 1.2.3. -- If the O.peration Requirement is met or is no longer applicable prior to expiration of the REMEDIAL REQUIREMENT (s) , completion of the REMEDIAL REQUIREMENT (s) is not required, unless otherwise stated. 1.2.3 Equipment removed from service or declared inoperable to comply with REMEDIAL REQUIREMENT (s) may be returned to service under administrative control solely to perform testing required to demonstrate OPERABILITY or the OPERABILITY of other equipment. This is an exception to OPERATION REQUIREMENT 1.2.2 for the system returned to service under administrative control to perform the testing required to demonstrate OPERABILITY, 1.3 General Surveillance Requirements 1.3.1 Surveillance Requirements shall be met during the applicable conditions specified in and for the associated Operation Requirement, unless otherwise stated in the Surveillance Requirement. Failure to meet a - Surveillance, whether such failure is experienced during the performance of the surveillance, or between performances of the Surveillance, shall be failure to meet the Operation Requirement. CLINTON-1 1-4 Rev.15-7/97 i
CPS-ODCM 1.3.2 The specified surveillance interval for each Surveillance Requirement is met if the Surveillance is performed l within 1.25 times the specified surveillance interval, as measured from the previous performance or as measured from the time a specified condition of the Surveillance Requirement is met. For surveillance intervals specified as "once", the above interval extension does not apply. If a REMEDIAL REQUIREMENT requires periodic performance on a "once per ..." basis, the above surveillance interval extension applies to each performance after the initial performance. Exceptions to this Surveillance Requirement are stated in the individual Surveillance Requirements. Failure to perform a surveillance within the specified time interval shall be a failure to meet- the Operation Requirement except as provided in Surveillance Requirement 1.3.3. Surveillances do not have to be performed on inoperable equipment or variables outside' specified limits. 1.3.3 If it is discovered that a surveillance was not performed within its specified surveillance interval, then compliance with the requirement to declare the Operational Requirement not met may be delayed, from the time of discovery, up to 24 hours or up to the limit of the specified interval, which ever is less. This delay period is to allow performance of the surveillance. If the surveillance is not performed within the delay period, the Operational Requirement must immediately be declared not met, and the applicable REMEDIAL REQUIREMENTS must be met. 1.3.4 Entry into a condition specified in and for an Operation Requirement 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. This provision shall not prevent entry into conditions specified for an Operation Requirement that.'is required to comply with REMEDIAL REQUIREMENT (s) or that are part of a shutdown of the unit. I l Surveillance Requirement 1.3.4 is only applicable for entry into a condition specified for an Operation Requirement in MODES 1, 2, and 3. l CLINTON-1 1-5 t L Rev.15-7/97 I
CPS-ODCM 1.4 Effluent Concentration Limit (lim) Calculation Requirements 1.4.1 The values found in 10CFR20 Appendix B, Table 2, Column 2 shall be used for all lim calculations in the ODCM. TABLE 1.1-1 SURVEILLANCE FREQUENCY NOTATION
)
NOTATION FREQUENCY S At least once per 12 hours. D At least once per 24 hours. W At least once per 7 days. M At least once per 31 days. O At least once per 92 days. SA At least once per 184 days. A At least once per 366 days. R At least once per 18 months (550 days) P Prior to each release. I S/U Prior to each reactor startup. NA Not applicable. Note: A frequency notation for a composite sample describes the time period over which the sample is to be g,I I composited. j i i 1 1 I CLINTON-1 1-6 Rev.15-7/97 ]
h CPS-ODCM 2.0 LIQUID EFFLUENTS 2.1 Introduction Liquid radwaste effluent released from CPS will meet 10CFR20 concentration limits at the point of discharge to the unrestricted area shown in Figure 2.1-1. This design and operation objective will be achieved at all times. Actual discharges of liquid radwaste effluent will normally occur on a batch basis and the average concentration at the point of discharge will be only a small percentage of the allowed limits. Refer to Clinton USAR Section 11.5 for a description of radiation monitoring, sampling and effluent control systems. Cumulative quarterly dose contributions due to radioactive effluents released to the unrestricted area. will be determined once every 31 days using NUREG-0133 and Regulatory Guide 1.109 methodology and parameters. 2.2 Liquid Radwaste Discharge Process Radiation Monitoring (PRM) System l This monitoring subsystem measures liquid radwaste effluent radioactivity prior to the effluent joining plant service water and circulating water dilutfon streams. A high radioactivity signal from this gamma scintillation detector automatically terminates the I liquid radwaste effluent release. The liquid radwaste effluent flow, variable from 10-60 GPM or 50-300 GPM, combines with Plant Service Water flow (minimum flow approximately 2000 GPM during plant shutdown periods depending on system loads) and Plant Circulating Water l flow (0-567,000 GPM) in the Seal Well prior to entering the 3.4-mile discharge flume to Lake Clinton (see Figure 2.5-1). 2.3 10CFR20 Release Rate Limits The Operation and Surveillance Requirements pertaining to l discharge of liquid radwaste effluent to the unrestricted area are specified in Section 2.3.1 as follows. CLINTON-1 2-1 Rev.15-7/97 L
CPS-ODCM 2.3.1 Liquid Effluent Concentration - Operation and Surveillance Requirements OPERATION REQUIREMENT The concentrati.on of radioactive material released in liquid effluent to UNRESTRICTED AREAS (see Figure 2.1-1) shall be limited to ten times the concentrations l 6" \ specified in 10CFR Part 20, Appendix B, Table 2, Column 2 for radionuclides other than dissolved or entrained noble gases. For dissolved or entrained noble the concentration shall be limited to 2 x 10~' gases, microcuries/ml total activity. This requirement applies during all releases via this pathway. REMEDIAL REQUIREMENT: I With the concentration of radioactive material released in liquid effluents to UNRESTRICTED AREAS exceeding the above limits, immediately restore the concentration to within the above limits. ; i SURVEILLANCE REOUIREMENTS 2.3.1.1 Radioactive liquid wastes shall be sampled and analyzed 1 according to the sampling and analysis program of Table k 2.3-1. j 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 assure that the concentrations at the point of release are maintained within the limits of the above Operation Requirement. To comply with the above requirements, setpoints will be calculated to assure that Seal Well concentrations do not exceed 10CFR20, Appendix B, Table 2, Column 2 values at i any time. l CLINTON-1 2-2 Rev.15-7/97 J
CPS-ODCM TABLE 2.3-1 RADIOACTIVE LIQUID WASTE SAMPLING AND ANALYSIS PROGRAM LIQUID LOWER LIMI'] MINIMUM RELEASE SAMPLING OF DETECTIC ANALYSIS TYPE OF ACTIVITY (LLD)* TYPE FREQUENCY FREQUENCY ANALYSIS ( Ci/ml) Batch Waste P P Principal Gamma Release Each Batch 5x10-7 Each Batch Emitters' Tanks' I-131 1x10-6 P M Dissolved and One Batch /M 1x10-5 Entrairred Gases * (Gamma Emitters) P Q H-3 1x10-5 Each Batch Composite.d Gross Alpha 1x10-7 P Q Sr-89, Sr-90 5x10-8 Each Batch Composite d Fe-55 ' 1x10-6 l D CLINT N-1 2-3 Rev.15-7/97
CPS-ODCM TABLE 2.3-1 (Continued) j l RADIOACTIVE LIQUID WASTE SAMPLING AND ANALYSIS PROGRAM TABLE NOTATIONS l
"The LLD is defined, for purposes of these requirements,-as the l smallest concentration of radioactive material in a sample that I 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 measurements system, which may include radiochemical separation: LLD = 4.66 se / [E x V x 2.22 x 10' x Y x exp" A") l Where: LLD is the "a priori" lower limit of detection as defined-above, as microcuries per unit mass or volume, , se is the standard deviation of the background counting rate l 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' is the number of disintegrations per minute per microcurie, Y is the fractional radiochemical yield, when applicable, A is the radioactive decay constant for the particular radionuclide ( sec~* ) and At for plant effluents is the elapsed time between the , ",, 6 midpoint of sample collection and the midpoint of the 1 counting interval (sec). < Typical values of E, V, Y and At should be used in the calculation. CLINTON-1 2-4 Rev.15-7/97 )
CPS-ODCM TABLE 2.3-1 (Continued) RADIOACTIVE LIQUID WASTE SAMPLING AND ANALYSIS PROGRAM TABLE NOTATIONS (Continued) It should be recognized that the LLD is defined as an a priori (before the fact) limit representing the capability of a measurement system limit for a particular and not as an a posteriori (after the fact) measurement.
'A 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.
- The principal gamma emitters are: Mn-54, Fe-59, Co-58, Co- 69, Zn-65, Mo-99, Cs-134, Cs-137, and Ce-141.
Ce-144 shall also be measured, but with an LLD of 5 x 10-6 pCi/ml. All identified radionuclides shall be reported in the Radioactive Effluent Release Report pursuant to Technical Specification 5.6.3 in a format outlined in Regulatory Guide 1.21, Appendix B, Revision 3, June 1974. d A 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.
- Dissolved and Entrained Kr-85m, Kr-87, and Kr-88.gases are: Xe-133,-Xe-135, Xe-138, CLINTON-1 2-5 nmr 1s-7/o7
CPS-ODCM 2.3.2 Liquid Radwaste Discharge PRM Setpoints To comply with the Operation Requirements of Section 2.3.1 and Section 2.7.1, the alarm / trip setpoints for liquid effluent monitors and flow' measurement devices
.are set to assure that the following equation is-satisfied:
cf/ (F _+ f) < Cum (1) Cu, = 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 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~efflu0nt stream.
F = the dilution water flow setpoints 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 effluent concentration (Cn.). The method by which this
~
is accomplished is illustrated in sections 2.3.2.1 through 2.3.2.5. 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: - CLINTON-1 2-6 mewm 15-7/@7 j
I 1 C PS - ODCM EiCi =E yCg+ E.C,4 E,C, + Cr + Cre , pCi/ml (2) where t EgC, = The sum of concentrations Cg of each measured gamma emitter g (including I-131) observed by gamma spectroscopy of the waste sample, pCi/ml. E.C. = The sum of concentrations C, of alpha emitters l ' (a) in liquid radwaste as measured in the most current QUARTERLY composite discharge tank sample, pCi/ml. l E.C. = The sum of concentrations C, of Sr-89/Sr-90 in l liquid radwaste as observed in the most current l QUARTERLY composite discharge tank sample, i pCi/ml. . C, = The measured concentration of._H-3 in liquid i radwaste as determined from analysis of the most current QUARTERLY composite discharge tank sample, pCi/ml. l ' Cre = The measured concentration of Fe-55 in liquid
- radwaste as observed in the most current QUARTERLY composite discharge tank sample, pCi/ml.
2.3.2.2 The measured radionuclide concentrations are used to l calculate a DILUTION EACTOR (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 l B, Table 2, Column 2 are met at the point of discharge to the unrestricted area. DF = SF[E i (Ci / lim 3)), dimensionless (3) ! = SF(Ig(cg /11mg) +I,(c /11m.) +I,(c /11m.) + (cr / lim 2) +cre /limrel l where ECi i = The measured concentrations ~C,, C., C., Cr, Cr. as defined in equation (2), Ci/ml. limi = The limiting concentration of the corresponding radionuclide from 10CFR20, Appendix B, Table 2, Column 2, pCi/ml. For dissolved or entrained noble gases, the concentration shall be limited ~ to 2E-04 pCi/ml total activity. CLINTON-1 2-7 Rev.15-7/97
CPS-ODCM 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, F .nx, t is calculated by the following equation: F tank =0. 9 ( Fon +t f ,ng) / DF, volume / time (4) where Fou = Minimum expected dilution water flow rate (Circulating and/or Service Water systems), g volume / time f t.nx = Maximum expected liquid radwaste tank effluent flow rate, volume / time 0.9 = Flow rate correction factor tm provide a 10% margin for variations in flow rates, dimensionless DF = The DILUTION EACTOR calculated by equation (3), dimensionless Equation (4) is valid only for DF>1; for DF<1, the i liquid radwaste tank effluent concentration meets the limits of 10CFR20 witho'it dilution and therefore F .nx t may assume any value not to exce.ed discharge pump capacity. 2.3.2.4 The liquid radwaste discharge PRM setpoint may now be specified based on the values of Z ii C (Eq.2) and F.nx t (Eq. 4 ) which were determined to provide compliance with the concentration limits of 10CFR20, Appendix B, Table 2, Column 2. The monitor response is primarily a gamma response and the actual setpoint is therefore based on EgC, (Eq.2) . The monitor setpoint, in counts per minute (cpm), which corresponds to the particular setpoint concentration, Cs, 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 proven more accurate than the monitor data. CLINTON-1 _ _ _ _ _ _ _ _ _ _ 2-8 Rov.15-7/97 l
)
l CPS-ODCM The set point concentration, Cs, is obtained by the j following equation: Cn = [ F .ng/ f.ct ] 9Eg C , pCi/ml t (5) where f.ct = The actual liquid radwaste effluent flow rate, volume / time If ( E .nx/ f.ct) >1, the value obtained for Cn is used to t l determine the monitor setpoint above background, ccpm, from either of the two methods described above. In the i case where ( E .nk/ f.ct ) < 1, no release may be made using t l the existing discharge parameter values (DF, F .ng, l f.ct) . t The setpoint concentration is conservative, even if F .nk is attainable, since the calculated flow rate t contains the SAFETY FACTOR, dilution flow rate and liquid radwaste tank effluent flow rate margins. l 2.3.2.5 To prevent spurious alarms, revise the Plant Service i Water Effluent PRM setpoint to coincide with the setpoint concentration, Cn, calculated by equation (5). This setpoint is valid only during periods of actual l , liquid radwaste discharges. l i i
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l 9 CLINTON-1 2-9 Rev.15-7/97
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C PS - O DCM 2.3.3 Plant Service Water Effluent PRM Setpoints Plant service water effluent continuously releases to the Seal Well where it mixes with circulating water effluent (if present) prior to entering Lake Clinton via the 3.4 mile discharge' flume. The plant service water effluent is not considered a radioactive discharge pathway unless liquid radwaste 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-emitting radionuclides. In addition, a quarterly composite of positive grab samples 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. l The Plant Service Water effluent PRM setpoint should be i established as close to background as practical to prevent spurious alarms, and yet assure an alarm should an inadvertent release occur. 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 follows: 2.3.3.1 Perform section 2.3.2.2, solving 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, DF., must be determined so that available dilution flows may be apportioned among simultaneous discharge pathways. The modified dilution factor is defined as: D F, = DF/Fx (6) where 3F is an administrative allocation factor which may be assigned any value between 0 and 1 under the condition that CLINTON-1 2-11 Rev.15-7/97
CPS-ODCM En (F3 )n <1 (7) and where n = the number of liquid discharge pathways for which DF >l and which are planned for simultaneous release. For simplicity, Fa may be assigned the value 1/n. Calculate F.nx t in equation (4) by substituting the value of DF, for DF and perform the calculation specified in section 2.3.2.4 to determine flow rate and PRM setpoints. 2.3.4 Shutdown Service Water (SX) Effluent PRM Setpoints shutdown Service Water, when initiated, is a potential continuous radioactive discharge pathway to the Ultimate Heat Sink (UHS) (see Figure 2.5-2). The SX effluent is not considered a radioactive discharge pathway unless any SX cooling load heat exchanger has been detected as failed. SX effluent sampling, analysis and setpoint 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 Setpoints The Fuel Pool Heat Exchanger Service Water is normally 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 leakage would be detected as described in section 2.3.3. The Fuel Pool Heat Exchanger Service Water effluent is considered a potential radioactive
) discharge pathway when SX replaces CCW as the heat sink for the fuel pool heat exchangers. To account for a potential release of CCW radioactivity to the Ultimate Heat Sink via SX, CCW will be sampled prior to placing "* j the Fuel Pool Heat Exchanger in the SX cooling mode and analyzed as discussed in section 2.3.3. The analysis results will then be used to establish Fuel Pool Heat Exchanger Service Water PRM and flow rate setpoints 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 Service Water Systems are considered abnormal events. Such events will be accounted for as unplanned releases in the RADIOACTIVE EFFLUENT RELEASE REPORT. 2.3.6 Component Cooling Water PRM Setpoints The Component Cooling water system is a potential continuous radioactive discharge pathway to the Service Water system due to the Component Cooling water system generally operating at a higher pressure. Component g+ Cooling provides cooling to components and heat exchangers that carry radioactive fluids or are in areas that could result in radioactive contamination if I the components are damaged. Except for the sampling -) requirement described in 2.3.5, sampling on this system is done on an as needed basis. The PRM setpoints are ' established using the methodology in Section 2.3.3. j CLINTON-1 2-12 Rev.15-7/@7 ]
CPS-ODCM 2.4 10CFRSO, Appendix I Release Rate Limits The Operation and Surveillance Requirements concerning j 10CFR50, Appendix I Release Limits are specified in section 2.4.1. Dose calculations for ensuring compliance with these limits are discussed in section 2.4.2. 2.4.1 10CFR50, Appendix I Release Rate Limits - Operation and Surveillance Requirements OPERATION REQUIREMENT The dose or dose commitment to a MEMBER OF THE PUBLIC from radioactive materials in liquid effluents released to UNRESTRICTED AREAS (see Figure 2.1-1) shall be limited: a. During any calendar quarter to less than or equal to 1.5 mrem to the total body and to less than or equal to 5 mrem to any organ, and b. During any calendar year to less than or equal to 3 mrem to the total body and to less than or equal to 10 mrem to any organ. This requirement applies at all times. REMEDIAL REQUIREMENT: With the calculated dose from the release of radioactive materials in liquid effluents 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 (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 REQUIREMENTS 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. l CLINTON-1 2-13 l ( _ - _ _ _ - . _ _ _ _ _ _ _ _ - - - - - - - - - - - - - - - - - - - - - - Rev.15-7/97 -j
CPS-ODCM 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: D3 = E [A i3 E" AT, CuFr] , mrem i (8) t= 1 where j D)
=
The cumulative calendar quarter or yearly dose to any organ j from liquid effluent for the , total release period, mrem AT, = The length of the tth release time period over I which Ce and F, are averaged for liquid i 1 releases, hours
~
=
Liquid Radwaste Tank Volume / Liquid Radwaste Discharge Flow Rate ! 1 Csi
= The average concentration of nuclide i in !
undiluted liquid effluent during release period ) Att for any liquid release, pCi/ml
=
Fs The near field average dilution factor for Ce i during any liquid effluent release, dimensionless. Defined as 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 ,
= Average Undiluted Liquid Waste Flow (9)
(Average Discharge Structure Flow) Z Z = The applicable dilution factor for Lake ' Clinton, dimensionless
= 1.0
= Tne composite ingestion dose commitment factor A13 for the total body or critical organ of an ADULT for radionuclide i, mrem /hr'per pCi/ml
= Ko [ (Uw/D,) + (UrBFi ) ]DF1 (10)
CLINTON-1 2-14 Rev.15-7/97 ,
1 CPS-ODCM where Ko = A units conversion factor, 1.14E+05 pCi-ml-yr/ pCi-liter-hr
=
(1.0E+06 pC1/pCi) (1.0E+03 ml/ liter) /8760 hr/yr U. = Annual water consumption by the maximum adult, O liter /yr D, = Dilution factor from the near field area to the nearest potable water intake, 1.0 Ur = Adult fish consumption rate, 21 kg/yr (Table E-5 of Regulatory Guide 1.109) BFi = Bioaccumulation factor for radionuclide i in fish, pCi/kg per pCi/ liter (Table 2.4-2 taken from Table A-1 of Regulatory Guide 1.109) DFi = Adult ingestion dose conversion factor for radionuclide 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 value's for A 13 as calculated by equation (10). The quarterly limits specified in the OPERATION
. REQUIREMENT at the beginning of this section represent one-half of the annual design objective of Section II.A of 10CFR50, Appendix I.
A I CLINTON-1 2-15 t Rev.15-7/97
CPS-ODCM TABLE 2.4-1 ADULT INGESTION DOSE COMMITMENT FACTORS - Au (mrem /hr per pCi/ml) l l ISOTOPE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI H-3 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 6.24E+03 6.24E+03 6.24E+03 6.24E+03 6.24E+03 I NA-24 4.06E+02 4.06E+02 4.06E+02 4.06E+02 4.06E+02 4.06E+02 4.06E+02 I P-32 1.39E+06 8.62E+04 5.36E+04 NO DATA NO DATA NO DATA 1.56E+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 6.57E+02 4.54E+02 1.06E+02 NO DATA NO DATA 2.53E+02 2.60E+02 1.04E+03 FE-59 2.44E+03 9.34E+02 NO DATA NO DATA 6.81E+02 8.13E+03 l 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 NI-65 1.26E+02 1.64E+01 7.40E+00 NO DATA NO DATA NO DATA 4.16E+02 I 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 7.36E+04 3.33E+04 NO DATA 4.92E+04 NO DATA 4.64E+04 ZN-69 4.92E+01 9.42E+01 6.55E+00 NO DATA 6.12E+01 NO DATA 1.41E+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 RB-88 No LATA 2.89E+02 1.53E+02 NO DATA NO DATA NO DATA 4.00E-09 4 RB-89 NO DATA 1.92E+02 1.35E+02 NO DATA NO DATA NO DATA 1.11E-11 I 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 NO DATA 6.67E+00 NO DATA NO DATA NO DATA 3.05E+03 Y-90 5.75E-01 NO DATA 1.54E-02 NO DATA NO DATA NO DATA 6.10E+03 Y-91m 5.43E-03 NO DATA 2.10E-04 NO DATA NO DATA NO DATA 1.60E-02 j Y-91 8.42E+00 NO DATA 2.25E-01 NO DATA NO DATA NO DATA 4.64E+03 Y-92 5.05E-02 NO DATA 1.48E-03 NO DATA NO DATA NO DATA 8.84E+02 Y-93 1.60E-01 NO DATA 4.42E-03 NO DATA NO DATA NO DATA 5.08E+03 ZR-95 2.40E-01 7.69E-02 5.20E-02 NO DATA 1.21E-01 NO DATA 2.44E+02 ZR-97 1.32E-02 2.67E 03 1.22E-03 NO DATA 4.04E-03 NO DATA 8.28E+02 NB-95 4.46E+02 2.48E+02 1.33E+02 NO DATA 2.45E+02 NO DATA 1.51E+06 MO-99 NO DATA 1.03E+02 1.96E+01 NO DATA 2.33E+02 No DATA 2.39E+02 TC-99m 8.86E-03 2.50E-02 3.19E-01 NO DATA 3.80E-01 1.23E-02 1.48E+01 TC-101 9.11E-03 1.31E-02 1.29E-01 NO DATA 2.36E-01 6.70E-03 3.94E-14 RU-103 4.42E+00 NO DATA 1.90E+00 NO DATA 1.69E+01 NO DATA 5.16E+02 RU-105 3.68E-01 NO DATA 1.45E-01 NO DATA 4.76E+00 NO DATA 2.25E+02 RU-106 6.57E+01 NO DATA 8.32E+00 NO DATA 1.27E+02 NO DATA 4.25E+03 AG-110m NO DATA NO DATA NO DATA 'NO DATA NO DATA NO DATA NO DATA TE-125m 2.57E+03 9.28E+02 3.43E+02 7.70E+02 1.04E+04 NO DATA 1.02E+04 TE-127m 6.47E+03 2.31E+03 7.89E+02 1.65E+03 2.63E+04 NO DATA 2.17E+04 TE-127 1.05E+02 3.77E+01 2.28E+01 7.79E+01 4.28E+02 NO DATA 8.30E+03 TE-129m 1.10E+04 4.10E+03 1.74E+03 3.78E+03 4.59E+04 NO DATA 5.54E+04 TE-129 3.00E+01 1.13E+01 7.31E+00 2.30E+01 1.26E+02' NO DATA 2.26E+01 TE-131m 1.65E+03 8.09E+02 6.74E+02 1.28E+03 8.19E+03 NO DATA 8.03E+04 TE-131 1.88E+01 7.87E+00 5.95E+00 1.55E+01 8.25F+01 NO DATA 2.67E+00 CLINTON-1 2-16 Rev.15-7/97 a
CI'S -O DCM TABLE 2.4-1 (cont'd) ADULT INGESTION DOSE COMMITMENT FACTORS - An (mrem /hr per Ci/ml) ISOTOPE BONE LIVER T. BODY
- THYROID KIDNEY LUNG GI-LLI TE-132 2.41E+03 1.56E+03 1.46E+03 1.72E+03 1.50E+04 NO DATA 7.37E+0/ 7 I-130 2.71E+01 7.99E+01 3.15E+01 6.78F+03 1. 2 SE4 02 NO DATA I-131 1.49E+02 2.13E+02 1.22E+02 6.88E+0.L 6.99E+04 3.66E+02 NO DATA 5.63E+01 1-132 7.28E+00 1.95E+01 6.81E+00 6.81E+02 3.10E+01 NO DA'1A I-133 5.09E+01 8.85E+01 2.70E+01 3.66E+00 1.30E+04 1.54E+02 NO DATA 7.96E+01 I-134 3.80E+00 1.03E+01 3.69E400 1.79E+02 1.64E+01 NO DATA I-135 1.59E+01 4.16E+01 9.00E-03 1.53E+01 2.74E+03 6.67E+01 NO DATA CS-134 2.97E+05 7.07Et05 5.78E+05 4.70E+01 NO DATA 2.29E+05 7.60E+04 1.24E+04 CS-136 3.11E+04 1.23E+05 8.84E+04 NO DATA CS-137 6.84E+04 9.37E+03 1.40E+04 3.81E+05 5.21E+05 3.41E+05 NO DATA 1.77E+05 5.88E+04 CS-138 2.64E+02 5.21E+02 1.01E+04 2.58E+02 NO DATA 3.83E+02 3.78E+01 BA-139 9.29E-01 6.60E-04 2.72E-02 2.22E-03 NO DATA 6.18E-04 3.75E-04 1.65E+00 BA-140 1.94E+02 2.44E-01 1.27E+01 NO DATA BA-141 4.50E-01 8.29E-02 1.40E-01 4.00E+02 3.40E-04 1.52E-02 NO DATA 3.1GE-04 1.93E-04 BA-142 2.04E-01 2.09E-04 1.28E-02 2.12E-10 NO DATA 1.77E-04 1.18E-04 2.89E-19 LA-140 1.49E-01 7.53E-02 1.99E-02 NO DATA NO DATA LA-142 NO DATA' 5.53E+03 7.65E-03 3.48E-03 8.66E-04 NO DATA NO DATA NO DATA CE-141 2.24E-02 1.51E-02 1.72E-03 2.54E+01 NO DATA 7.03E-03 NO DATA 5.78E+01 CE-143 3.94E-03 2.92E+00 3.23E-04 NO DATA CE-144 1.17E+00 1.28E-03 NO DATA 1. 09E+02 4.88E-01 6.26E-02 No DATA 2.89E-01 NO DATA PR-143 5.50E-01 2.20E-01 3.94E+02 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 ND-147 3.76E-01 4.21E-04 NO DATA 2.59E-10 4.34E-01 2.60E-02 NO DATA 2. 54E-01 ~ NO DATA 2.08E+03 W-187 2.95E+02 2.47E+02 8.63E+01 NO DATA NO DATA NO DATA 8.09E+04 l NP-239 2.84E-02 2.80E-03 1.54E-03 NO DATA 8.72E-03 NO DATA 5.74E+02 {
- 3.12 x 10'
**Less than 10-"
I l l 9 CLINTON-1 2-17 I Rev.15-7/97 1
1 CPS-ODCM TABLE 2.4-2 BIOACCUMULATION FACTORS -BF, (pCi/kg per pCi/ liter) FRESHWATER ELEMENT FISH H 9.0E-01 C 4.6E+03 Na 1.0E+02 P 1.0E+05 Cr 2.0E+02 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 2.5E+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 Pr 2.5E+01 Nd 2.5E+01 W ' 1.2E+03 Np 1.0E+01 l CLINTON-1 2-18 Rev.15-7/97
CPS-ODCM TABLE 2.4-3 l ADULT INGESTION DOSE FACTORS -DFi (mrem /pCi ingested) ISOTOPE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI H-3 NO DATA 1.05E-07 1.05E-07 1.05E-07 1.05E-07 1.0$E-07 1.05E-07 l C-14 2.84E-06* 5.68E-07 5.68E-07 5.68E-07 5.68E-07 5.68E-07 NA-24 1.70E-06 5.68E-07 1.70E-06 1.70E-06 1.70E-06 1.70E-06 1.70E-06 1.70E-06 P-32 1. U.-04 1.20E-05 7.46E-06 NO DATA NO DATA NO DATA CR-51 NO DATA 2.17E-05 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 l 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 FE-59 4.34E-06 1.09E-06 1.02E-05 3.91E-06 NO DATA NO DATA 2.85E-06 3.40E 05 l CO-58 NO DATA 7.45E-07 1.67E-06 NO DATA NO DATA NO DATA CO-60 1.51E-05 2.14E-06 No DATA 4.72E-06 NO DATA NO DATA NO DATA NI-63 1.30E-04 4.02E-05 i 9.01E-06 4.36E-06 NO DATA NO DATA NO DATA 1.88E-06 I ( NI-65 5.28E-07 6.86E-08 3.13E-08 NO DATA NO DATA NO DATA 1.74E-06 i CU-64 NO DATA 8.33E-08 3.91E-08 NO DATA 2.10E-07 ZN-65 4.84E-06 NO DATA 7.10E-06 1.54E-05 6.96E-06 NO DATA 1.03E-05 NO DATA 9.70E-06 ! ZN-69 1.03E-08 1.97E-08 1.37E-09 NO DATA 1.28E-08 NO DATA BR-83 2.96E-09 NO DATA NO DATA 4.02E-08 NO DATA NO DATA NO DATA 5.79E-08 i BR-84 NO DATA NO DATA 5.21E-08 NO DATA NO DATA NO DATA 4.09E 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 t l RB-89 NO DATA 4.01E-08 2.82E-08 NO DATA NO DATA NO DATA 2.33E-21 l 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 , SR-91 5.67E-06 NO DATA 2.29E-07 NO DATA NO DATA NO DATA 2.70E-05
.' 4 l
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 Y-91m 9.09E-11 NO DATA 3.52E-12 NO DATA NO DATA NO DATA 2.67E-10 l Y-91 1.41E-07 NO DATA 3.77E-09 NO DATA NO DATA NO DATA 7.76E-05
! Y-92 8.45E-10 NO DATA 2.47E-11 NO DATA NO DATA NO DATA 1.48E-05 i Y-93 2.68E-09 NO DATA 7.40E-11 NO DATA NO DATA No DATA 8.50E-05 l 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 1.05E-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 NO DATA 9.99E-06 TC-99m 2.47E-10 6.98E-10 8.89E-09 NO DATA 1.06E-08 3.42E-10 4.13E-07 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 i ! RU-106 2.75E-06 NO DATA 3.40E-07 N0 DATA 5.31E-06 NO DATA 1.78E-04 l AG-110m 1.60E-07 1.48E-07 8.79E-08 NO DATA 2.91E-07 NO DATA 6.04E-05 i 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 8.25E-07 1.73E-06 2.75E-05 NO DATA 2.27E-05 TE-127 1.10E-07 3.95E-08 2.38E-08 8.15E-08 4.48E-07 NO DATA 8. 68 E- 06 TE-129m 1.15E-05 4.29E-06 1.82E-06 3.95E-06 4.80E-05 NO DATA 5.79E-05 TE-129 3.14E-08 1.18E-08 7.65E-09 2.41E-08 1. 32 E NO DATA 2.37E-08 TE-131m 1.73E-06 8.46E-07 7.05E-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 , l CLINTON-1 2-19 Rev.15-7/97
CPS-ODCM TABLE 2.4-3 (cont'd) ADULT INGESTION DOSE FACTORS - DF i (mrem /pCi ingested) ISOTOPE DONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI TE-132 2.52E-06 1.63E-06 1.53E-06 1.80E-06 1.57E-05 NO DATA I-130 7.56E-07 7.71E-05 2.23E-06 8.80E-07 1.89E-04 3.48E-06 NO DATA 1.92E-06 I-131 4.16E-06 5.95E-06 3.41E-06 1.95E-03 1.02E-05 NO DATA I-132 1.57E-06 2.03E-07 5.43E-07 1.90E-07 1.90E-05 8.65E-07 NO DATA 1.02E-07 I-133 1.42E-06 2.47E-06 7.53E-07 3.63E-04 4.31E-06 NO DATA 2.22E-06 I-134 1.06E-07 2.88E-07 1.03E-07 4.99E-06 4.58E-07 NO DATA 2.51E-10 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-08 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 3.56E-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 IA-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 1.2SE-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 6.45E-11 NO DATA 3.65E-10 NO DATA 2.40E-05 02.84 x 10* 0*Less than 10-** CLINTON-1 2-20 Rev.15-7/97 j
l CPS-ODCM i FIGURE 2. 5-1 l LIQUID RADWASTE TREATMENT SYSTEM
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- Monitors required by Section 2.7 WF01S Floor Drain OWZO1P Chem. Wst. 2WF04T Floor Drain OWE 02PA,B, and C Evaporator Evap. Tank Pump Evaporator Tank Waste Samp. Tk Pumps WF013 Floor Drain OWE 01FA,B, and C OWZO1T Chem. Waste OWE 01TA and B Evaporator Waste Filters Evaporator Tank Excess Water Tanks OWZOIS Chemical OWE 01DA,B, and C IWF04P Fir. Drn. OWE 01PA and B Waste Evaporator Waste Demins Evap. Tank Pump Excess Water Tank Pumps WF04T Floor Drain OWE 02TA,B, and C 2WF04P Fir. Drn. IPR 036 Service Evaporator Tank Waste Sample Tks. Evap. Tank Pump Water PRM O'PR040 Liquid RW Discharge PRM CLINTON-1 2-21 Rev.15-7/97
CPS-ODCM FIGURE 2.5-2 SHUTDOWN AND FUEL POOL HEAT EXCHANGER SERVICE WATER EFFLUENT MONITORS SHUTDOWN SHUTDOWN SERVICE SERVICE RHR HEAT WATER WATER EXCHANGER "A* I FUEL POOL HEAT SHUTDOWN EXCHANGER SERVICE I SERVICE WATER SHUTDOWN SINK , 140P "A" OTHER SYSTEM SERVICE WATER EFFLUENT "A" 1RIX-PR004* LOADS 1RIX-PR038* /\ \/ EVEL POOL COOLING HEAT EXCHANGER *A* COMPONENT COMPONEN* COOLING \ \ COOLING MATER / -
/ NATER l EVEL POOL COOLING HEAT EXCHANGER "B" fHUTDOWN V WATE ULTIMTE \/ /\
HEAT EVEL POOL HEAT SERVICE WATER EFFLUENT *B.R SINK EXCHANGER SERVICE LOOP =B' 1RIX-PR039 WATER PRM I 1RIX-PR005* j g7 SHUTDOWN SHUTDO601 RHR HEAT SERVICE SERVICE EXCHANGER *B" WATER WATER
. NORMAL COOLING. SUPPLY - COMPONENT COOLING WATEk ,
EMERGENCY COOLING SUPPLY - SHUTDOWN SERVICE WATER !
- Monitors required by Section 2.7 l
1RIX-PR038 Shutdown Service 1RIX-PR005 Fuel Pool Heat Water Effluent "A" Exchanger Service Water PRM 1RIX-PR039 Shutdown Service 1RIX-PR004 Fuel Pool Heat Water Effluent "B" Exchanger Service Water PRM i
)
CLINTON-1 2-22 Rev.15-7/97 . J
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T l l l CPS-ODCM 2.5 Liquid Radwaste Treatment System l 2.5.1 Liquid Radwaste Treatment System - Operation and i Surveillance Requirements OPERATION REQUIREMENT I The liquid radwaste treatment system shall be OPERABLE. The appropriate portions of the system (Figure 2.5-1) shall be used to reduce the radioactive materials in l liquid wastes prior to their discharge when the projected ( doses due to the liquid effluent to UNRESTRICTED 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 l requirement applies at all times. REMEDIAL REQUIREMENT: l With radioactive liquid waste being discharged without treatment and in excess of the above lindts and any portion of the liquid radwaste treatment system not in operation prepare and submit to the Regional l Administrator of the Regional Office of the NRC within'30 ' days a Special Report that includes the following information:
- 1. Explanation of why liquid radwaste was being
] discharged without treatment, identification of any r inoperable equipmcnt or subsystems, and the reason for the inoperability.
- 2. Action (s) taken to restore the inoperable equipment to OPERABLE status, and l 3. Summary description of action (s) taken to prevent a recurtance.
SURVEILLANCE REQUIREMENTS 2.5.1.1 Doses due to liquid releases to UNRESTRICTED AREAS shall be projected at least once per 31 days in accordance with the methodology and parameters described in Section l 2.4.2. 2.5.1.2 The liquid radwaste treatment shall be demonstrated OPERABLE by meeting the Operation Requireme.nts of Section 2.3.1 and 2.4.1. l l l l CLINTON-1 2-24 Rev.15-7/97
CPS-ODCM 2.5.2 Temporary Liquid Radwaste Hold-Up Tanks The use of temporary liquid radwaste hold-up tanks may occur at CPS. To comply with Operational Requirements Manual (ORM) 2.4.4, the curie limit for liquid radwaste stored in such tanks may be calculated using the methodology presented in Appendix B of NUREG-0133 (BWR-RATAFR code), but limited to less than or equal to 10 curies, excluding tritium and dissolved or entrained noble gases. 2.6 Doses'From Other Significant Liquid Effluent Pathways Section 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 crops, 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 addi'ional dose increment greater than or equal to 10 percent of the total from all other existing pathways. Methode 'or calculating doses from' other potentially significant liquid effluent pathways are presented in Appendix A to Regulatory Guide 1.109. When it is determined that other liquid effluent pathways
) ~ do exist, the Regulatory Guide 1.109 Appendix A aquations and parameters will be used in lieu of site-specific data to determine a pathway's significance.
2.7 Radioactive Liquid Effluent Monitoring Instrumentation 2.7.1 Radioactive Liquid Effluent Monitoring Instrumentation Operation and Surveillance Requirements
- OPERATION REQUIREMENT The radioactive liquid effluent monitoring instrumentation channels shown in Table 2.7-1 shall be OPERABLE with their alarm / trip setpoints set to ensure that the limits of Section 2.3.1 are not exceeded. The alarm / trip 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. ,
.) CLINTON-1 2-25 Rev.15-7/97
CPS-ODCM REMEDIAL REQUIREMENT:
- a. With a ra'ioactive d liquid 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 channels ,
OPERABLE, comply with the REMEDIAL REQUIREMENT shown in Table 2.7-1. Restore the inoperable instruments to OPERABLE status within 30 days and, if unsuccessful, explain in the next Radioactive l Effluent Release Report why the inoperability was not corrected in a timely manner. SURVEILLANCE REQUIREMENTS - 2.7.1.1 Each rad t active liquid effluent monitoring instrumentation control shall be demonstrated OPERABLE'by performance of the CHANNEL CHECK, SOURCE CHECK, CHANNEL ; CALIBRATION and CHANNEL FUNCTIONAL TEST at the frequencies shown in Table 2.7-2. ) l 4 CLINTON-1 2-26 Rev.15-7/97
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CPS-ODCM TABLE 2.7-1 (Continued) RADIOACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION TABLE NOTATION (a) Channel OPERABILITY shall include the capability of the Main Control Room Central Control Terminal (MCR-CCT) to provide the alarm status of the applicable radiation monitor channel (s) . REMEDIAL REQUIREMENT REMEDIAL With the number of channels OPERABLE less than R'IQUIREMENT required by the Minimum Channels OPERABLE 1 requirement, effluent releases may continue via this pathway provided that prior to initiating a release:
- a. At least two independent samples are analyzed in accordance with Section 2.3.1.1, and
- b. At least two technically qualified members' independently verify the release rate calculations and discharge line valving:
Otherwise, suspend release of radioactive _ i effluents via this pathway. ! REMEDIAL a. With the communication link or the MCR-CCT l '* ' REQUIREMENT inoperable perform CHANNEL CHECK using local 2 monitor indication within 8 hours and at least once per 8 hours thereafter. ;
- b. With the monitor otherwise inoperable, effluent releases via this pathway may continue provided that at least once per 12 hours, grab samples are collected and analyzed for radioactivity at a Lower Limit of Detection of 5.0 x 10-' Ci/cc for the .
. Principal Gamma Emitters. The Principal Gamma Emitters are: Mn-54, Fe-59, Co-58, Co-60, Zn-65, Mo-99, Cs-134, Cs-137, and Ce-141.
Ce-144 shall be measured with an LLD of 5.0 x 10-' pCi/cc. Dissolved and Entrained Gases (gamma emitters only? shall be measured with an LLD of 1.0 x 10-5 pCi/cc. These Dissolved and Entraineu Gases are: Xe-133, Xe-135, Xe-138, Kr-85m, Kr-87, and Kr-88. CLINTON-1 2-28 Rev.15-7/97
CPS-ODCM TABLE 2.7-1 (Continued) I ! RADIOACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION TABLE NOTATION REMEDIAL With the number of channels OPERABLE less than l REQUIREMENT required by the Minimum Channels OPERABLE 3 requirement, effluent releases via this pathway may continue provided the flow rate is estimated at least once per 4 hours during actual releases. Pump performance curves generated in place may be used to estimate flow. All flows diverted from Plant Service Water must be taken into account when estimating dilution flow when Plant Service Water is the only dilution source. REMEDIAL With the number of channels OPERABLE less than REQUIREMENT required by the Minimum Channels OPERABLE 4 requirement, liquid additions to this tank may continue provided the tank liquid level is estimated during all liquid additions to the tank. l
-)
CLINTOII-1 2-29 Rev.15-7/97
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CPS-ODCM TABLE 2.7-2 (Continued) RADIOACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION SURVEILLANCE REQUIREMENTS TABLE NOTATIONS (1) The CHANNEL FUNCTIONAL TEST shall also demonstrate that automatic isolation of this pathway occurs and that the MCR-CCT provides annunciation and event display in response to each of the following conditions:
- 1. Instrument indicates measured levels above the alarm / trip (HIGH) setpoint. ,
i
- 2. Detector failure (LOW EAIL, HI EAIL).
- 3. Sample flow failure (EXTERNAL EAIL) .
l
- 4. Instrument not set in normal operate mode tUNINITIALIZED, CALIBRATE, MAINTENANCE, or STANDBY.)*
(2) The CHANNEL FUNCTIONAL TEST shall also demonstrate that the MCR-CCT responds with annunciation and event display to each of the following conditions: i
- 1. Instrument indicates measured levels above the alarm 1 (HIGH) setpoint.
- 2. Detector failure (LOW EAIL, HI EAIL).
- 3. Sample flow failure (EXTERNAL FAIL).
- 4. Instrument not set in normal operate mode ,
(UNINITIALIZED, CALIBRATE, MAINTENANCE, or STANDBY.)* oA demonstration of automatic isolation of the release pathway is not applicable to this condition. ' CLINTON-1 2-32 Rev.15-7/97 j l
CPS-ODCM TABLE 2.7-2 (Continued) ) RADIOACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION SURVEILLANCE REQUIREMENTS l l TABLE NOTATIONS (3) The initial CHANNEL CALIBRATION shall be performed using one or more of the reference standards certified by the National Institute of Standards and Technology (NIST) or using standards that have been obtained from suppliers that participate in measurement assurance activities with NIST. 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 hours on days which continuous, periodic, or batch releases are made. (5) Determine that channel communication is established to the MCR-CCT.
)
I CLINTON-1 2-33 Rev.15-7/97
CPS-ODCM 3.0 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 Purge and mechanical vacuum pump discharge may be considered short term releases. There are two gaseous effluent release points to the environment: the Common 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 Engineered 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)
- 2) Containment Building Ventilation
- 3) Turbine Building Ventilation '
- 4) Radwaste Building Ventilation
- 5) Auxiliary Building Ventilation
- 6) Fuel Building Ventilation
- 7) Auxiliary Building Refrigerant Purge
- 8) Laboratory Ventilation System
- 9) Counting / Equipment Decon Rooms Ventilation
- 10) Steam Packing Exhauster
- 11) Mechanical Vacuum Pump
- 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 HVAC Stack, with the exception of input numbers 7 through 10, can be monitored prior to entering the stack. Figure 3.1-1 delineates the CPS site boundary for , implementation of gaseous effluent 10CFR20 and 10CFR50, Appendix I Release Rate Limits. 1 CLINTON-1 3-1 Rev .15-7 /97 i
CPS-ODCM 3.2 Gaseous Effluent Release Point Monitoring 3.2.1 HVAC Stack Process Radiation Monitoring (PRM) System The HVAC Scack inputs are monitored for radioactivity j prior to discharge to the environment by the HVAC Stack PRM. The PRM' detector configuration provides effluent monitoring using nine (9) channels as follows:
- 1) Beta scintillator for particulates
- 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 subtraction f
! 5) Beta scintillator for low range ~ noble gas l l 6) Energy-compensated Geiger-Mueller (G-M) detector j for high range noble gas
- 7) Energy-compensated G-M detector for gamma area l subtraction l . 8) Sample pressure indication at the KVAC PRM
- 9) Sample-flow rate-indication at the HVAC PRM l
This monitor has no control function but annunciates in the Main Control Room where proper response actions will be initiated in accordance with CPS procedures. 3.2.2 SGTS Stack Process Radiation Monitoring (PRM) System As' discussed in.section 3.1, the SGTS is used to reduce l post-accident concentrations of radioactivity in the ! primary and secondary containment via filter trains. The SGTS Stack PRM 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) Beta scintillator for particulates ,'
- 2) Gamma scintillator for iodine l
i { L CLINTON-1 3-2 Rev.15-7/97 L:
CPS-ODCM
- 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 detector to account for the radon / thoron contribution to the beta particulate measurement
- 8) Sample pressure indication at the SGTS PRM
- 9) Sample flow-rate indication at the SGTS PRM This monitor has no control function but annunciates in the Main Control Room where proper response actions will be initiated in accordance with CPS procedures.
3.3 Main Condenser Off-Gas Monitoring System 3.3.1 Pre-Treatment Air Ejector Off-Gas Process Badiation Monitor (PNH) The Pre-Treatment Off-Gas PRM monitors hydrogen recombiner 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-compensateo G-M detector mounted in a gas volume. The monitor has no control function but annunciates in the Main Control Room where proper response actions will be initiated in accordance with CPS procedures. 1 l l l l CLINTON-1 3-3 Rev.15-7/97
CPS-ODCM 3.3.2 Post-Treatment Air Ejector Off-Gas Process Radiation Monitor ( PIUi) The Post-Treatment Off-Gas PRM monitors the gaseous radioactivity at upstream, intermediate or downstream sections of the charcoal adsorber beds prior to the effluent entering the station HVAC Stack for release to the environn.ent (see Figure 3.3-1). The PRM detector configuration is as described for the HVAC Stack PRM (Section 3.2.1). The monitor has two control functions. Upon detection of noble gas activity in excess of the ALERT setpoint, the 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 is shown in Figure 3.3-1. 3.4 10CFR20 Release Rate Limits I The Operation and Surveillance Requirements concerning 10CFR20 Release Rate Limits are specified in Section 3.4.1. 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 REQUIREMENT The dose rate due to radioactive materials released in gaseous effluents from the site to areas at and beyond the SITE BOUNDARY (see Figure 3.1-1) shall be limited to the following:
- a. For noble gases: 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 l
CLINTON-1 3-4 Rev.15-7/97
CPS-ODCM
- b. For iodine-131, for iodine-133, for tritium, and for all radionuclides in particulate form with l half lives greater than 8 days: Less than or equal to 1500 mrem /yr to any organ.
This requirement applies at all times. REMEDIAL REQUIREMENT: With the dose rate (s) exceeding the above limits, ! immediately restore the release rate to within the l above limit (s). l l SURVEILLANCE REQUIREMENTS l 3.4.1.1 The dose rate due to noble gases in gaseous effluents shall be determined to be within the above limits in l accordance with the methodology and parameters in Section 3.4.2 by obtaining representative samples and l Fd ' g- ! 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 be, ,
. determined to be within the above limits in accordance
, with the methodology and parameters in Section 3.4.3 by l 0N-L' obtaining representative samples and performing i analyses in accordance with the sampling and analysis l program specified in Table 3.4-1. l CLINTON-1 3-5 Rev.15-7/97 (
f CPS-ODCM a TABLE 3.4-1 RADIOACTIVE GASEOUS WASTE SAMPLING AND ANALYSIS PROGRAM ! i i ( " Lower Limit i l of Detection Sampling Analysis Type of LLD Gaseous Release Type Frequency Frequency Activity Analysis (pCi/cc) l A. Station HVAC Exhaust
- 1. Noble Gas and W# W* Principal Gamma 1.0 x 10
Tritium Release Grab Emitters
- 1.0 x 10-
- H-3 l 2. Iodines Release Continuous' W 4 I-131 1.0 x 10~2# ld l
I-133 1.0 x 10~8' l 3. Particulates Release Continuous 3 W' Principal Gamma 1. 0 x 10-11 j M Emitters
- 1.0 x 10~22 l9 l Composite Gross Alpha Activity Q Sr-89, Sr-90 1.0 x 10-21 Composite Activity B. Standby Gas Treatment System Exhaust, when flow exists
! 1. Noble Gas and W W Principal Gamma 1.0 x 10~ l# l Tritium Release Grab Emitters
- 1.0 x 10~
l l H-3
- 53. Iodines Release Continuous
- W' I-131 1.0 x 10'**
I-133 1.0 x 10~2' ! 3. Particulates Release Continuous 3 W' Principal Gamma 1.0 x 10"** l M Emitters
- 1.0 x 10'**
Composite Gross Alpha Activity
- Q Sr-89, Sr-90 1.0 x 10"**
Composite Activity , l l CLINTON-1 3-6 Rev.15-7/97 l
CPS-ODCM TABLE 3.4-1 (Continued) RADIOACTIVE GASEOUS WASTE SAMPLING AND ANALYSIS PROGRAM TABLE NOTATIONS
'The 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: LLD = 4. 66 s3/[E x V x 2.22 x 10' x Y x exp - Au) Where: LLD is the "a priori" lower limit of detection as defined above, as microcuries per unit mass or volume, se is the standard deviation of the background counting rate or of the counting rate of a blank sample as appropriate, as counts per minute,s,= (R ' where Rsw = background counts t=the background count time E is the counting efficiency, as counts per disintegration, V is the sample size in units of mass or volume, 2.22 x 10' is the number of disintegrations per minute per microcurie, Y is the fractional radiochemical yield, when applicable, A is the radioactive decay constant for the particular radionuclide (s ec-* ) and At for plant effluents is the elapsed time between the midpoint of sample collection and the midpoint of the counting interval- (sec) . Typical values of E, V, Y, and At should be used in the calculation. CLINTON-1 3-7 Rev.15-7/97
C PS-ODCM TABLE 3.4-1 (Continued) RADIOACTIVE GASEOUS WASTE SAMPLING AND ANALYSIS PROGRAM TABLE NOTATIONS (Continued) It should be recognized that the LLD is defined as an a priori (before the fact) limit representing the capability of a measurement system and not as an a posteriori (after the fact) limit for a particular measurement. 2 The principal gamma emitters are: 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 Ce-144 in iodine and particulate releases. Other gamma peaks that are identifiable, together with those of the above nuclides, shall be analyzed and reported in the Radioactive Effluent Release Report pursuant to Technical Specification 5.6.3 in the format outlined in Regulatory Guide 1.21, Appendix B, Revision 1, June 1974.
- Sampling 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.
'The ratio of the sample flow rate to the sampled stream flow rate shall be known for the time period covered by each dose or dose rate calculation made in accordance with Sections 3.4.1,
, 3.5.1 and 3.5.2.
' Samples shall be changed at least once per 7 days and analysis shall be completed within 48 hours after changing, or after removal from sampler. Sampling shall also be performed at least once per 24 hours for at least 7 days following each shutdown, startup, or THERMAL POWER change exceeding 15% of RATED THERMAL POWER in 1-hour period and analyses shall be completed within 48 hours of chahging. When samples collected for 24 hours'or less 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 on the applicable PRM (HVAC or SGTS) lj shows that effluent activity has increased more than a factor of 3. CLINTON-1 3-8 Rev.15-7/97 l
CPS-ODCM 3.4.2 Dose Rate Due to Noble Gases In order to comply with Section 3.4.1. (a), the dose rate at or beyond the site boundary due to noble gases shall be calculated as follows: Dt = EK i i ( (X/Q),Qi,] (1)
=
total body dose rate at time of release, mrem / year D, = E (L +1.1Mi ) [ (X/0),Oi,] 1 i (2)
= skin dose rate at time of release, mrem / year The terms in the above equations are defined in section 3.4.3.
3.4.3 Dose Rate Due to Radioiodines, Particulates and Tritium In order to comply with Section 3.4.1(b), organ dose. rates due to radioiodines (I-131, I-133), particulates with half-lives > 8 days and tritium shall be calculated as follows: D. = epi 1 3[(X/Q),Qi ] (3)
= 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 emissions for each identified noble gas radionuclide i, mrem /yr per pCi/m' Li = The skin dose factor due to beta emissions for each identified noble gas radionuclide i, mrem /yr per pCi/m' M3 = The air dose factor due to gamma emissions for each identified noble gas radionuclide i, mrad /yr per- pCi/m3 (1.1 mrem / mrad converts air dose to skin dose) CLINTON-1 3-9 Rev.15-7/97
CPS-ODCM P,3 = The dose factor for non-noble gas radionuclide i and organ j which includes l pathway transport parameters, receptor usage factors and the dosimetry of the I exposure. The dose factors for the inhalation, mrem /yr per Ci/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. On, = The release rate of noble gas radionuclide i in gaseous effluent from l mixed-mode release points, pCi/sec On, = The release rate of non-noble gas i radionuclide i in gaseous effluent from mixed-mode release points, pCi/sec (X/0), = The highest calculated' average relative concentration for any area at or beyond l the site boundary from mixed-mode l releases, sec/m l Do is calculated for each of six organs and the total l body; the maximum Do value is then used to determine compliance with Section 3.4.l(b) . The factors K i, L,i and Mi relate the radionuclide l 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-1 of Regulatory Guide 1.109 after multiplying the values by the conversion 10' pCi/ Ci. 10CFR20 organ dose rate calculations are limited to the inhalation pathway only. Section 3. 4. l (a) is - applicable to the unrestricted area location characterized by the (X/Q) value which results in the maximum total body or skin dose commitment. Should the total body and skin locations differ, 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. CLINTON-1 3-10 Rev.15-7/97
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1 CPS-ODCM TABLE 3.4-3 INHALATION PATHWAY DOSE RATE FACTORS (CHILD) - P y I 3 (mrem /yr per Ci/m ) ORGAN BONE LIVER T. BODY THYROID KIDNEY LUNG 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 9.88E+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 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 2.87E+03 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 LATA 1.11E+06 3.44E+04 CO-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 2.75E+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 5.85E-02 1.42E+03 1.02E+04 BR-83 NO DATA NO DATA 4.74E+02 NO DATA NO DATA NO DATA LT 3.70E-15** BR-84 NO DATA NO DATA 5.40E+02 NO DATA NO DATA NO DATA LT 3.70E-15 BR-85 NO DATA NO DATA 2.53E+01 NO DATA NO DATA NO DATA LT 3.70E-15 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
'B-89 NO DATA 3.45E+02 2.90E+02 NO DATA NO DATA NO DATA 1.89E+00 A-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 6.49E+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 2.68E+05 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 DATA NO DATA 7.44E+04 3.89E+05 ER-95 1.90E+05 4.18E+04 3.70E+04 NO DATA 5.96E+04 2.23E+06 6.11E+04 ZR-97 1.88E+02 2.72E+01 1.60E+01 NO DATA 3.89E+01 1.13E+05 3.51E+05 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 2.92E+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+00 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+04 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 7.07E+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 5.88E-02 2.05E+03 1.33E+03 CLINTON-1 3-12 Rev.15-7/97 1
CPS-ODCH TABLE 3.4-3 (cont'd) INHALATION PATHWAY DOSE RATE FACTORS (CHILD) - Py (mrem /yr per pCi/m ) OPGAN BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE TE-132 4.81E+02 2.72E+02 2.63E+02 3.18E+02 1.77E+Cs 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 I-131 4.81E+04 4.81E+04 2.73E+04 7.88E+04 NO DATA 2.84E+03 I-132 1.62E+Q 2.12E+03 4.07E+03 1.88E+03 1. 94 E4 05 6.2SE+03 NO DATA 3.20E+03 I-133 1.66E+04 2.03E+04 7.70E+03 3.85E+16 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 I-135 4.92E+03 8.73E+03 4.14E+03 7.92E+05 1.34E+04 NO DATA 4.44E+03 CS-17,4 6.51E+05 1.01E+06 2.2SE+05 NO DATA 3.30E+05 1.21E+05 3.84E+03 CS-136 6.51E+04 1.71E+05 1.16E+05 NO DATA 9.55E+04 1.45E+04 4.18E+03 CS-137 9.07E+05 0.2SE+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 6.21E+02 6.81E+01 2.70E+02 BA-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. 64 E+03 2.74E+00 LA-140 6.44E+02 2.25E+02 7.55E+01 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+04 2.90E+03 NO DATA 8.55E+03 5.44E+05 5.66E+04 CE-143 3.66E+02 1.99E+02 2.88E+01 NO DATA 8.36E+01 1.15E+05 1.27E+05 CE-144 6.77E+06 2.12E+06 3.62E+05 NO DATA 1.17E+06 1.20E+07 3.89E+05 PR-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 1.8bE-02 3.00E-03 NO DATA 9.77E-03 1.57E+03 1.97E+02 "D-147 1.08E+04 8.73E+03 6.81E+02 NO DATA 4.81E+03 3.28E+05 8.21E+04
*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 3.35E+01 2.35E+01 NO DATA 9.73E+01 5.81E+04 6.40E+04
- l.12 x 10"
- Less than 3.70 x 10*
CLINTON-1 3-13 Rev.15-7/97
CPS-ODCM l TABLE 3.4-4 l l LOCATION OF MEMBERS OF THE PUBLIC WITHIN THE CPS SITE BOUNDARY AND THEIR ASSOCIATED OCCUPANCY FACTORS
- l Distance Occupancy l Location (mile / meter) Sector (hrs /yr)
Road 0.3/495 SE 243(1) Agricultural Acreage (2) 0.9/1372 SSW 966(3) Clinton Lake 0.2/335 NW 2208(4) ! Department of 0.8/1287 ESE 2208(5) Conservation Recreation Area - Residence 0.8/1219 SW 8760 Residence 1.5/2414 WSW 8760 Residence 1.7/2736 SSE 8760 i (1) Assumes travel on road for forty minutes per day. (2) Maximum farm acreage (276) within site boundary. (3) Assumes 3.5 hours in field per acre 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.
- Doses for such MEMBERS OF THE PUBLIC are provided in the Radioactive Effluent Release Report as given in Section 6.3.2.
CLINTON-1 3-14 t Rev.15-7/97 j
CPS-ODCM 3.5 10CFR50, APPENDIX I 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. Dose calculations for ensuring compliance with these limits are discussed in Sections 3.5.3 and 3.5.4. i 3.5.1 Noble Gas Dose - Operation and Surveillance I Requirements l OPERATION 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) shall be limited to the following:
- a. During any calendar quarter: Less than or equal to 5 mrad for gamma radiation and less than or equal to 10 mrad for beta radiation, and
- b. During any calendar year: Less than or equal to 10 mrad for gamma radiation and less than or equal to 20 mrad for beta radiation.
This requirement applies at all times. I REMEDIAL REQUIREMENT:
- a. With the calculated air dose from radioactive nobles gases in gaseous effluents exceeding 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.
l CLINTON-1 3-15 Rev.15-7/97
1 l CPS-ODCM SURVEILLANCE REQUIREMENTS 3.5.1.1 Cumulative dose contributions for the current calendar quarter and current calendar year for noble gases shall l be determined in accordance with the methodology and parameters described in Section 3.5.3 at least once per 31 days. 3.5.2 Iodine-131, Iodine-133, Tritium, 'and Radionuclides in
! Particulate Form - Operation and Surveillance Requirements OPERATION REQUIREMENT t
The dose to a MEMBER OF THE PUBLIC from iodine-131, ! iodine-133, tritium, and all radionuclides in ! particulate form with half-lives greater than 8 days in I 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 7.5 mrem to any organ, and
- b. During any calendar year: Less than or equal to 15 mrem to any organ.
This requirement applies at all times. REMEDIAL REQUIREMENT:
- a. With the calculated dose from the release of iodine-131, iodine-133, tritium, and radionuclides in particulate form with half lives greater than 8 days, in gaseous effluents exceeding any~of the above limits prepare and submit to the 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 that subsequent releases will be in compliance with the above limits.
CLINTON-1 3-16 Rev.15-7/97
CPS-ODCM SURVEILLANCE REQUIREMENTS 3.5.2.1 Cumulative dose contributions for the current calendar quarter and current calendar year for iodine-131, iodine-133, tritium, and radionuclides in particulate form with half-lives greater than 8 days shall be determined in accordance with the methodology and parameters 31 days. described in Section 3.5.4 at least once per 3.5.3 Noble Gas Air Dose Equations The air dose at or beyond the site boundary due to noble gases released in gaseous effluent will be determined using the following equations. 3.5.3.1 During any calendar quarter or calendar year, for gamma radiation:
~
Dy = 3.17 x 10~'E M i i[ (X/Q) .Qi.] (4) 3.5.3.2 During any calendar quarter or calendar year, for beta radiation:
=
Dp 3.17 x 10-eE1Ni [ (X/Q).Qi.] (5) where Mi = The gamma air dose factor for each identified noble gas radionuclide i, mrad / year per pCi/m 3 (Mi values are listed in Table 3.4-2). Ni = The beta air dose factor for each identified noble gas radionuclide i, mrad / year per pCi/m 3 (Ni values are listed in Table 3.4-2). (X/Q). = The highest calculated average relative l concentration from mixed-mode release l
~
points for areas at or beyond the site i boundary, sec/m*. l Q1. = The total release of noble gas radionuclide i for long-term releases l from mixed-mode release points, pCi. ' Releases shall be cumulative over the calendar quarter or year, as appropriate. CLINTON-1 3-17 Rev.15-7/97 ;
CPS-ODCM 3.17 x 10-" = The inverse of the number of seconds in a year. Section 3.5.1 noble gas dose calculations are evaluated at the site boundary location where maximum air doses prevail. Should the beta and gamma locations differ, the selected location shall be that which minimizes allowable release rates due to the gamma component. 3.5.4 Radiciodines, Particulates and Tritium Dose Equations The dose to an individual at or beyond the site boundary due to radiciodines (I-131, I-133), tritium and particulates with half-lives > 8 days, will be determined suing the follow equation: for any calendar quarter or calendar year, De = 3.17 x 10-*I R.gW Qi, i (6) where Qi, = The releases of radionuclide 1 (I-131, I-133, tritium and particulates) for releases from mixed-mode release points, pCi. Releases shall be cumulative over the calendar quarter or year, as appropriate. (D/Q), = The relative deposition from mixed-mode release points for areas at or beyond the site boundary, m-*.
= The dispersion parameter for estimating the W.
dose to an individual at a controlling location for mixed-mode releases.
= (X/Q)., sec/m', for the inhalation pathway at the location of the critical receptor.
= (D/Q) , m*, for the food and ground plane pathways at the location of the critical receptor.
3.17 x 10-8 = The inverse of the number of seconds in a year. CLINTON-1 3-18 Rev.15-7/97
CPS-ODCM Roi, = The dose factor for each identified radionuclide 2 i, age group (a) and organ j, m -mrem / year per pCi/sec or mrem / year per pCi/m'. 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 i pathways exist as determined by the most current land use census. 3.5.4.1 Dose Factor For Radionuclide 1 (R n) The R y values used to calculate D pin equation (6) are determined separately for each of the potential exposure pathways, namely:
~
- Inhalation (I)
- Ground Plane Contamination (G)
- Grass-Cow / Goat-Milk (C)
- Grass-Cow-Meat (M)
- Vegetation (V)
The R.13 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 Pathway Factor, R*.i3 R* y = K' (BR) . (DFA1 ) ., mrem / year per pCi/m 3 (7) where
~
\
K' = A units conversion constant, 10' pCi/pCi (BR). = The breathing rate of the receptor age group (a), m'/ year
=
1400 (infant)
=
3700 (child)
=
8000 (teen and adult) Values for (BR). are obtained from NUREG ,0133, pg. 32 .i CLINTON-1 3-19 Rev.15-7/97
CPS-ODCM l ( D FAi ) . = The organ inhalation dose factor for receptor ! of age group (a) for radionuclide i, mrem /pCi. Values for (DFA ), were obtained i l from Tables E-7 through E-10 of Regulatory Guide 1.109 and are presented in Tables 3.5-1 ! through 3.5-4 of.this manual. l 3.5.4.1.2 Calculation of the Ground Plane Pathway Factor, R i R i
= K'K" (SF) (DFG ) [ (1-e * * ) /11 } ,
i (8) 2 m -mrem / year per pCi/sec l where K' = A units conversion constant, 10' pCi/pCi l K" = A units conversion constant, 8760 hour / year l SF = The shielding factor, dimerisionless l ! = 0.7 as suggested in Table E-15 of Regulato#y Guide 1.109 DFG 1 = The ground plane dose conversion factor for 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. Ai = The decay constant for radionuclide i, sec* 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',13 R .n = K' (Or(U p) / ( A t + L)] F,( r) (DFL )i , (9)
( fp f,/Y, + (1-f f.) p e i*h/Y ] e~ i*f, m'-mrem /yr per Ci/sec where K' = A units conversion constant, 10' pCi/pCi CLINTON-1 3-20 Rev.15-7/97
CPS-ODCM Or = The cow / goat feed consumption rate, kg(wet)/ day U.p = The receptor's milk consumption rate for age group (a), liters / year Yp '= The agricultural productivity by unit area of pasture feed grass, kg/m* Y. = The agricultural productivity by unit area of stored feed, kg/m F. = The stable element transfer coefficient for milk, days / liter r = Fraction of deposited activity retained on feed grass, dimensionless (DFLi ) . = The organ ingestion dose factor for radionuclide i and the receptor in age group (a), mrem /pCi. Values for (DFL 1 ), were obtained from Tables E.11 through E-14 of Regulatory Guide 1.109'and are presented i'n Table 3.5-6 through 3.5-9 of this manual. A1 = The decay constant for radionuclida i, sec-1 Av = The decay constant for removal of activity *on leaf and plant surfaces by weathering, sec-
= 5. 73 x 10-' sec-* (corresponding to a 14-day half-life) ,
= The transport time from pasture to animal, to tr milk, to receptor, sec ta = The transport time from pasture to' harvest, to animal, to receptor, sec fp = Fraction of the year that the cow / goat is on pasture, dimensionless
= Fraction of tne cow / goat feed that is pasture f.
grass while the cow / goat is on pasture, dimensionless The input parameters for calculating RP.13 are I listed in Table 3.5-10. ' CLINTON-1 3-21 Rev.15-7/97 J
CPS-ODCM , Tritium The concentration of tritium in milk is based on its airborne concentration rather than the deposition. c Rr = K ' K" F,QrU,p (DFL ) , i 0.75(0.5/H), mrem /yr per Ci/m' (10) where K" = A units conversion constant, 10' gm/kg H = The absolute atmospheric humidity
= 8 gm/m' (NUREG-0133, p. 34) 0.75 =
The fraction of total feed that is water, dimensionless 0.5 = The ratio of the specific activity of the feed grass water to the atmospheric water, dimensionless l The other parameters are as defined in the calculation of R* y Carbon - 14 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**O or C*'02 . The concentration of carbon-14 in milk is therefore based upon its airborne concentration assuming that the vegetation C*'/C ratio is the same as the local atmospheric C**/C ratio.
- R"2 4 =
K' K"F.QrU,p (DFL 1 ) , p (0.11/0.16) , mrem /yr per pCi/m' (11) where p = Fractional equilibrium ratio, dimensionless
=
Ratio of the total annual C-14 atmospheric release time to the total annual photosynthesis time (4400 hours) not to exceed unity
= 1.0 CLINTON-1 3-22 Rev.15-7/97 i
C PS-ODCM 0.11 = Natural carbon fraction of total plant mass, dimensionless 0.16 = Atmospheric natural carbon concentration, gm/m' The Cother parameters are as defined in the calculation of R r 3.5.4.1.4 Calculation of the Grass-Cow-Meat Pathway Factor, R".13 R".13 = [ K ' Or (U,p) / ( A t + L) ] Fr (r) (DFL ), 1 [ fp f./Yp + [ (1-f f.) p /Y.] e i*h) e i's, m*-mrem /yr per Ci/sec (12) where K' = A units conversion constant, 10' pCi/pCi U,p = The receptor's meat consumption rate for age group (a), kg/ year ' Fr = The stable element tra'nsfer coefficient, days /kg
=
T'
- t. The transport time from slaughter of meat animal to receptor, seconds tn = The transport time from crop field to receptor, seconds (DFLi ) . = The organ ingestion dose factor for radionuclide 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*.13 are listed in Table 3.5-11. All other terms are as definr'd for equations (9) and (10). Tritium The concentration of tritium in meat is based on its airborne concentration rather than the deposition. R", = K' K" FrQrU.p (DFL ) . [0.75(0.5/H)], i i mrem /yr per pCi/m' (13) . ) CLINTON-1 3-23 Rev.15-7/97 j
CPS-ODCM The terms in equation (13) are as defined in equations (10) and (12). Carbon - 14 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**O or C**02 . The concentration of carbon-14 in meat is therefore based upon its airborne concentration assuming that the vegetation C*d/C ratio is the same as-the local atmospheric C"/C ratio. R"3 4 = K' K"FrQrU p (DFL 1 ), p (0.11/0.16) , mrem /yr per pCi/m' (14) The terms in equation (14) are as defined in equations (11) and (13). 3.5.4.1.5 Calculation of the Vegetation Pathwap Factor, R*m
=
R*.13 K' [ (r) / [Yv ( 1A + () ) ) (DFL1 ). [U' ft e i*L + U'.fg e i*h), m*-mrem /yr per pCi/sec (15)
- where K' =
A units conversion constant, 10' pCi/pCi U'. = The consumption rate of fresh leafy vegetation by the receptor in age group (a), kg/ year U*. = 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, dimensionless 4 f, = The fraction of the annual intake of stored vegetation grown locally, dimensionless t.t = The average time between harvest of leafy vegetation and its consumption, seconds tn = The average time between harvest of stored vegetation and its consumption, seconds CLINTON-1 3-24 Rev.15-7/97
CPS-ODCM Yv- = the vegetation area density, kg/m' (DFLi ) . = The organ ingestion dose factor for radionuclide 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*.13 are listed in Table 3.5-12. All other terms are as defined for equations (9) and (14). Tritium The concentration of tritium in vegetation is based on its airborne concentration rather than the deposition. S R*r = K ' K" (U'. f t + U .fg ) (DFL1 ) . [0.75(0.5/H)], mrem /yr per pCi/m (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-14 is assumed to be released as an oxide, either C"O or i C"(b. The concentration of carbon-14 in vegetation is therefore based upon its airborne concentration assuming that the vegetation C"/C ratio is the same as the local atmospheric C"/C ratio. V 8 Ru = K ' K" (U'. f t + U .f,) (DFL1 ) . p (0.11/0.16) , mrem /yr per pCi/m' (17) The. terms in equation (17) are as defined in equations (11) and (15) . The pathway dose rate factors ( R*.13 , R .13 , R V.13, R".13 , R"1 ) , by age group are listed in Table 3.5-13 through 3.5-31. 3.6 Gaseous Radwaste (Offgas Treatment) 3.6.1 Gaseous Radwaste (Offgas Treatment) System - Operation and Surveillance Requirements CLINTON-1 3-25 Rev.15-7/97
CPS-ODCM ( OPERATION REQUIREMENT The GASEOUS RADWASTE (OFFGAS) TREATMENT SYSTEM shall be in operation. This requirement applies whenever the main condenser steam jet air ejector system is in operation. REMEDIAL REQUIREMENT:
- a. With gaseous radwaste from the main condenser air ejector system being discharged without treatment for more than 7 days, 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. 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.
.\ SURVEILLANCE REQUIREMENT 3.6.1.1 The GASEOUS RADWASTE (OFFGAS) TREATMENT SYSTEM shall be verified to be in operation once every 12 hours when the main condenser air ejector is in use to ensure that the main condenser offgas treatment system is functioning.
NOTE When 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 may be calculated to account for the increased fractions of short-lived noble gases. The noble gas release fractions shall be based either on actual measured values or on design basis noble gas concentration fractions (30-minute delay) in the primary coolant offgas. CLINTON-1 3-26 Rev.15-7/97
CPS-ODCM 3.7 Ventilation 'xhaust E Treatment 3.7.1 Ventilation Exhaust Treatment System - Operation and Surveillance Requirement OPERATION REQUIREMENT The VENTILATION EXHAUST TREATMENT SYSTEM (VETS) 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 exceed 0.3 l mrem to any organ in a 31-day period. This requirement applies at all times other than when the VETS is undergoing routine maintenance. REMEDIAL REQUIREMENT:
- a. With gaseous waste being discharged without treatment and in excess of the above limit, prepare and submit to the Regional Administrator l
l of the Regional Office of the NRC within 30 days a Special Report that includes the following information:
- 1. Explanation of why gaseous radwaste was_being
!s discharged without treatment, identification I
- of any inoperable equipment or subsystems, l 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. -
SURVEILLANCE REQUIREMENTS l 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.* ! *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'O.3 mrem and the VETS is capable of reducing the projected impact to less than 0.3 mrem, the VETS shall be used.
)
CLINTON-1 3-27 Rev.15-7/97
CPS-ODCM 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. 3.8 Effluent Monitor Setpoint Calculations Gaseous effluent Process Radiation Monitor (PRM) alarm setpoints shall be calculated to ensure that the instantaneous dose rate in unrestricted areas due to noble gases released do not exceed 500 mrem / year to the total body and 3000 mrem / year to the skin. The initial
- setpoints were calculated using the BWR/ GALE code l radionuclide mix obtained for CPS; when the actual l radionuclide mix can be determined, it will be used for l setpoint calculations. The PRM setpoints are based on the instantaneous noble gas dose rates and are applied at the point of which the effluent enters an unrestricted area.
Due to PRM limitations, non-noble gas setpoints will not be implemented to demonstrate compliance with Section 3.4.1(b). Compliance with the organ dose rate limitation is demonstrated during performance of sampling and analysis activities required by Table 3.4-1. I Both total body and skin dose setpoints will be calculated and the more restrictive limit applied to the respective PRM. The actual setpoi: used may be lower than the restrictive limit since tue two release i points will be partitioned such that their sum does not l exceed 100 percent of the restrictive limit. The l percentages used to partition the release points could vary at plant discretion to accommodate plant operational conditions. In no case will the combined releases due to variations in the PRM setpoints result in effluent limits being exceeded. 3.8.1 Total Body Dose Rate Setpoint i 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 relationship: fy = Cu/ (E Co) , dimensionless i (18) CLINTON-1 3-28 Rev.15-7/97 4 ( __ ___ 1
l CPS-ODCM where C i3 = The measured concentration of identified noble gas radionuclide i in gaseous effluent release path j, pCi/cc The maximum acceptable re' lease rate of all noble gases in release path j to comply with Section 3.4.1 is calculated by using the equation: 013
=
500 F /[(X/Q)3E (K F33)], pCi/sec 3 i i (19) where
= The maximum acceptable release rate of all Or3 noble gases in release path j, pCi/sec F3 =
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
=
(X/0)3 The highest calculated average relative concentration of release path j at the site , boundary l Ki = The total body dose factor due to gamma emissions of noble gas radionuclide i as ' listed in Table B-1 of Regulatory Guide 1.109 and Table 3.4-2 of this manual, mrem /yr per , pCi/m* ) f i3 = The fraction as defined by equation (18), dime'nsionless The total maximum acceptable concentration setpoint of noble gas radionuclides in release path j is calculated using the following equation: - Cr3 = C T3 /R3 , pCi/cc (20) where
= The total maximum acceptable concentration Cr3 i setpoint of all noble gases in release path i j, pCi/cc l
CLINTON-1 3-29 Rev.15-7/97 l
.)
CPS-ODCM
=
Or> The maximum acceptable release rate of all noble gases in release path j determined from equation (19), pCi/sec R3 = The effluent release rate of release point j, cc/sec 3.8.2 Skin Dose Rate Setpoint To ensure compliance with the section 3.4.1(a) skin dose rate limit, PRM setpoints shall be calculated using the methodology presented in Section 3.8.1 and by substituting the following equation for equation (19): 3000F3 / [(X/Q)3 E (L +1.1M a33) ] , pCi/sec
=
Os3 1 i i (21) where Os3
= The masimum acceptable release rate of all noble gares in release path j, pCi/sec F3 =
Total dose rate allocation factor assigned to i 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 re,lative concentration of release path j at the site boundary Li = The skin dose factor due to gamma emissions for each identified noble gas radionuclide i, mrem /yr per pCi/m', as listed in Table 3.4-2 of this manual. 1.1 = An air dose to skin dose equivalent conversion factor, mrem / mrad Mi = The air dose factor due to gamma emissions for each identified noble gas radionuclide i, mrad /yr per pCi/m', as listed in Table 3.4-2 of this manual f i3 = The fraction defined by equation (18) . CLINTON-1 3-30 Rev.15-7/97 {
CPS-ODCM The calculated total body and skin maximum acceptable concentration setpoints are compared and the more restrictive setpoint used. A safety factor may also be applied to the concentration setpoint calculated by equation (20) to compensate for statistical fluctuations and measurement errors. 3.9 Radioactive Gaseous Monitoring Instrumentation 3.9.1 Offgas Radiation Monitoring Instrumentation - Operation and Surveillance Requirements OPERATION REQUIREMENT The offgas radiation monitoring instrumentation channels shown in Table 3.9.1-1 shall be OPERABLE, with their alarm / trip setpoints within the specified limits. This requirement applies during operation of the main condenser air ejector (s). REMEDIAL REQUIREMENT: l
- a. With a radiation monitoring instrumentation channel alarm / trip setpoint exceeding the value shown in Table 3.9.1-1, adjust the setpoint to within the limit within 4 hours or declare the channel inoperable.
- b. With one or more radiation monitoring channels l inoperable, comply with the REMEDIAL REQUIREMENT specified by Table 3.9.1-1.
SURVEILLANCE REQUIREMENTS 3.9.1.1 Each of the above required radiation monitoring instrumentation channels shall be demonstrated OPERABLE by the performance of the CHANNEL CHECK, SOURCE CHECK, CHANNEL FUNCTIONAL TEST and CHANNEL CALIBRATION at the frequencies shown in Table 3.9.1-2. ) CLINTON-1 3-31 Rev.15-7/97
T LN E A I M _ DE R 5 6 E I 7 7 M E U R EQ . R N O I c d T ' c A T P 'cc c IT / N RN / i i E TI i C _ M /O C A A U MP R RT 5 N N . T AE 0 0
- S LS N 5 I
A 7 1 <~ _ - G 1 N
. I R
9 O 3 T I E N L O B M A S T N L O E I ND T NE A AL I D HB *
- A CA 1 1
?
R R 1 1 ME S UP A M I O G N F I F M O s - g
- a f e n e ee l i m c tc N ffG f b d f e i ai O rO o i o I Oeo t v Rv T lt t Nyv s e e A tbi n to n y D wD T non e eir gvPdci o S o eNo m eg lg N m ni nit ttn Fn E M t atratae nai y a M t i U a e Rco Atmmia ans u
err er R eMt rM u l u T rRi tR Phgsnat rl f oa ma irome l ws ps C S tPv D N - i t iaoluee fl e ae O I est rac oa ss HGMAATR EFM SM . . S PgA Pg a b c P . . C 1 2
CPS-ODCM TABLE 3.9.1-1 (Continued) OFFGAS RADIATION MONITORING INSTRUMENTATION TABLE NOTATIONS a Alarm only. b A channel may be placed in an inoperable status for up to 1 hour for the purpose of performing surveillances. c Radioactivity concentration expected at the monitor location is a noble gas mix with a 2.9-minute decay. d Radioactivity concentration expected at the monitor location is a noble gas mix released from the off-gas treatment system. e Channel OPERABILITY shall include the capability of the Main Control Room Central Control Terminal (MCR=CCT) to provide the alarm status of the applicable radiation monitor ! channel (s) . ! REMEDIAL REQUIREMENT REMEDIAL REQUIREMENT a. With the MCR-CCT inoperable, 5
- 1. Perform a CHANNEL CHECK using local monit'or indication within 8 hours and at least once per 8 hours thereafter, and
- 2. Restore the MCR-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 l action taken to restore the inoperable equipment to OPERABLE status, l i CLINTON-1 3-33 Rev.15-7/97
CPS-ODCM i TABLE 3.9.1-1 (Continued) OFFGAS RADIATION MONITORING INSTRUMENTATION l
. TABLE NOTATIONS
- 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
- 2. The post-treatment air ejector off gas PRM high, range noble gas activity monitor is OPERABLE, or the provisions of REMEDIAL REQUIREMENT 6-b are in effect. -
I REMEDIAL REQUIREMENT a. With the MCR-CCT inoperable, 6
- 1. Perform a CHANNEL CHECK using local
) monitor indication within 8 hours and at least once per 8 hours thereafter, and
- 2. Restore the MCR-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.
CLINTON-1 3-34 Rev.15-7/97
l i CPS-ODCM TABLE 3.9.1-1 (Continued) OFFGAS RADIATION MONITORING INSTRUMENTATION TABLE NOTATIONS
- b. With the Post-treatment Off gas PRM High Range Noble Gas Activity Monitor otherwise inoperable, effluent releases via this pathway may continue provided grab samples are taken at least once per 8 hours, and a noble gas gamma isotopic analysis performed within 24 hours.
REMEDIAL
. REQUIREMENT 7
With the number of channels OPERABLE less than required by the minimum channels OPERABLE requirement, effluent releases via this pathway may continue provided the flow rate is estimated at least once per 8 hours. - l l l l 'i l I ' l l i CLINTON-1 3-35 Rev.15-7/97
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)
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)
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. T F 9 N E
3 M U E R L T E B S C K A N RC A A T T UE OH C M D N N @ G S N I R O h T I N L O EK M NC I I NE ' D D N AH 'D D O HC I C T A I D A s c g R a gt i n g - i S - f e na r ee A f f l b i m dof mu es tc G f r O ai . F O o o ito t a Rv F t t N yv u se - e O tsi n toAn yM wD N nan e eir o S o O ego m gvPdi e lg I ni nt tt Fn T m te M ta atraae na i A al y e Rco ns eRe er . T Atmia ucl u N ebt rM h i rme l wi ps E roi TR gsnarl f ov ma C' M TNv P D U it i aol ee fl e ae O R eMt ss HGMATR EFD SM
- T rRc oa . . .
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'C I 1 2 I, ; i l l ;If I
i CPS-ODCM l TABLE 3.9.1-2 (Continued) ' OFFGAS RADIATION MONITORING INSTRUMENTATION SURVEILLANCE REQUIREMENTS ) l TABLE NOTATION I a i Automatic isolation of valve IN66-F060 shall be demonstrated during the CHANNEL CALIBRATION. I i (1) The CHANNEL FUNCTIONAL TEST shall also demonstrate that the MCR-CCT responds with annunciation and event display to each ! of the following conditions- i 1 l l
- 1. Instrument indicates measured levels above the alarm / trip (HIGH) setpoint.
- 2. Detector failure (LOW EAIL, HI EAIL) .
l 1
- 3. Sample flow failure (EXTERNAL FAIL). -
L 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 l participate in measurement assurance activities with NIST. 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 l quality or radioactive sources that have been related to the i initial calibration. . (3) The CHANNEL CHECK shall also determine that channel l communication is established to the MCR-CCT. 1
. i l 1 l i i
l 1
\
l
. i l
l l l CLINTON-1 3-37 Rev.15-7/97 I J
CPS-ODCM 3.9.2 Radioactive Gaseous Effluent Monitoring Instrumentation
- Operation and Surveillance Requirements OPERATION REQUIREMENT I
l The radioactive gaseous effluent monitoring ! instrumentation channels shown in Table 3.9.2-1 shall be OPERABLE with their alarm / trip setpoints set to ensure that the limits of Section 3.4.1 and Technical Specification 3.7.5 are not exceeded. The alarm / trip l setpoints of these channels shall be determined and l adjusted in accordance with the methodology and ! parameters in this manual. This requirement applies as shown in Table 3.9.2-1. REMEDIAL REQUIREMENT: i a. With a radioactive gaseous effluent monitoring instrumentation channel alarm / trip setpoint less l conservative than required by the above requirement, immediately suspend the release of radioactive gaseous effluents monitored by the l affected channel, or declare the channel inoperable. b. With less than the minimum number of radioactive 8 gaseous effluent monitoring instrumentation l channels OPERABLE, comply with the REMEDIAL REQUIREMENT specified in Table 3.9.2-1. Restore the inoperable instrumentation to OPERABLE status i within 30 days and, if unsuccessful, explain in the next Radioactive Effluent Release Report l pursuant to Technical Specification 5.6.3 why this L inoperability was not corrected in a timely manner. - SURVEILLANCE REQUIREMENTS 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. CLINTON-1 3-38 Rev.15-7/97
fl fi 7
,. , 9 p g /
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CPS-ODCM l TABLE 3.9.2-1 (Continued) RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION TABLE NOTATIONS a At all times. b During' standby gas treatment system operation. l l c A channel may be placed in an inoperable status for up to 1 l hour for.the purpose of performing surveillances. d Channel OPERABILITY shall include the capability of the Main Control Room Central Control Terminal (MCR-CCT) to provide the alarm status of the applicable radiation monitor channel (s). e Filter media (particulate collection patch for particulates and charcoal cartridge for iodines) in place with an
-operating sample pump constitutes an iodine / particulate sampler. -
REMEDIAL REQUIREMENT
- I REMEDIAL REQUIREMENT a. With the communication link OR the MCR-CCT lfd[g inoperable, perform a CHANNEL CHECK 8 using local monitor indication within 8 hours and at-least once per 8 hours thereafter.
- b. With the noble gas activity monitor channel (s) otherwise inoperable, effluent i releases via this pathway may continue provided grab samples are taken at least once per 8 hours and analyzed for gross noble gas activity within 24 hours.
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 hours after the channel has been declared inoperable, samples required by Table 3.4-1 are continuously collected with auxiliary sampling equipment. REMEDIAL With the number of channels OPERABLE less than REQUIREMENT required by the minimum channels OPERABLE 10 requirement, effluent releases via t'his pathway may continue provided the flow rate is estimated at least once per 4 hours. CLINTON-1 3-40 Rev.15-7/97
7 9
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CPS-ODCM TABLE 3.9.2-2 (Continued) RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION SURVEILLANCE REQUIREMENTS TABLE NOTATIONS a At all times, b During operation of the standby gas treatment system. G(1) The CHANNEL FUNCTIONAL TEST shall also demonstrate that the MCR-CCT responds with annunciation and event display to each of the following conditions:
- 1. Instrument indicates measured levels above the alarm (HIGH) setpoint.
- 2. Detector failure (LOW EAIL, HI EAIL).
- 3. Sample flow failure (EXTERNAL EAIL) .
- 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 intended range of energy 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. 9(3) The CHANNEL CHECK shall also determine that channel communication is established to the MCR-CCT. t l CLINTON-1 3-42 Rev.15-7/97
7 _ Y . l R e y 9 a D A ms n a r / 7 D N in p u E U to s t - T O i e m l 5 c B st d o u L 1 _ Y R # R i eii u c c S .
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CPS-ODCM l FIGURE 3.3-1 l MAIN CONDENSER OFF-GAS TREATMENT SYSTEM
$ NMZ003A -
IN66D005A
/ , ; =; y f & ,
W W I ir IN66D010B d v 8l z IN6600ll l T _\ ICA01AA SCA01A8 - - - IN66D005B IN6.*D016 ll IN66D012 IN66D013 OCA0lTA ),M
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MAINMmf EXHAUST SOTS EXHAUST STACK
- Monitors required by Sections 3.9.1 and 3.9.2 ICD 01A Main OCA01TA CV 1N66B010B CondInser IN66D013 1RIX-PR035 Separator Tank Cooler Charcoal A Condenser B off-Gas Post Adsorber Treatment PRM 1CA01AA Steam OCA01TB CV 1N66Z003A Jat Air IN66D016 HEPA 1RIX-PR041 Separator Tank Dessicant Filter Ejector A B Dryer A Off-Gas Post Treatment PRM 1CA01AB Steam IN66D005A IN66 ZOO 3B jet Air ORIX-PR001 ORIX-PR003 Recombiner A Dessicant HVAC Stack PRM Standby Gas Ejsetor B Dryer B #1 Treatment PRM OCA01PA IN66D005B Condr.nser IN66B011 Gas ORIX-PR002 ORIX-PR004 Recombiner B Cooler HVAC Stack PRM Standby Gas Vacuum (CV) #2 Pump A Treatment PRM p OCA01PB CV IN66B010A Pump B IN66D012 1RIX-PR034 l Cooler Charcoal off-Gas Condenser A Adsorber Pretreatment PRM CLINTON-1 3-44 Rev.15-7/97
CPS-ODCM TABLE 3.5-1 INHALATION DOSE FACTORS FOR INFANT - ( D FAi ) , (mrem per pCi inhaled) NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI H-3 l 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 0.03E-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-55 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 NI-63 2.42E-04 1.46E-05 8.29E-06 NO DATA NO DATA 1.49E-04 1.73E-06 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 EN-69 3.85E-11 6.91E-11 5.13E-12 NO DATA 2.87E 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 DR-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 3.99E-07 2.05E-07 NO DATA NO DATA NO DATA 2.42E-07 RB-89 NO DATA 2.29E-07 1.47E-07 NO DATA NO DATA NO DATA 4.87E-08 i 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 E-91 6.83E-08 NO DATA 2.47E-09 NO DATA NO DATA 3.76E-05 5.24E-05 .a-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 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 Y-92 1.17E-08 NO DATA 3.29E-10 NO DATA NO DATA 1.75E-05 9.04E-05 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-05 1.45E-05 NO DATA 2.22E-05 1.25E-03 1.55E-05 ER-97 1.07E-07 1.83E-08 8.36E-09 NO DATA 1.85E-08 7.88E-05 1.00E-04 Na-95 1.12E-05 4.59E-06 2.70E-06 NO DATA 3.37E-06 3.42E-04' 9.0$E-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 TC-101 4.65E-14 5.88E-14 5.80E-13 NO DATA 6.99E-13 4.17E-07 6.03E-07 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 RU-106 6.20E-05 NO DATA 7.7E-06 NO DATA 7.61E-05 8.26E-03 1.17E-04 AG-110m 7.13E-06 5.16E-06 3.57E-06 NO DATA 7.00E-06 2.62E-03 2.36E-05 TE-125m 3.40E-06 1.42E-06 4.70E-07 1.16E-06 NO DATA 3.19E-04 9.22E-06 _ TE-127m 1.19E-05 4.93E-06 1.48E-06 3.4BE-06 2.68E-05 9.37E-04 1.95E-05 TE-127 1.59E-09 6.81E-10 3.49E-10 1.32E-09 3.47E-09 7.39E-06 1.74E-05 TE-129m 1.01E-05 4.35E-06 1.59E-06 3.91E-06 2.27E-05 1.20E-03 4.93E-05 TE-129 5.63E-11 2.48E-11 1.34E-11 4.82E-11 1.25E-10 2.14E-06 1.88E-05 I TE-131m 7.62E-08 3.93E-08 2.59E-08 6.38E-08 1.89E-07 1.42E-04 8.51E-05 TE-131 1.24E-11 5.87E-12 3.57E-12 1.13E-11 2.85E-11 1.47E-06 5.87E-06 CLINTON-1 3-45 Rev.15-7/97 j
CPS-ODCM TABLE 3.5-1 (continued) INHALATION DOSE FACTORS FOR INFANT - (DFAi ), (mrem per pCi inhaled) NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI l
.TE-132- 2.66E-07 1.69E-07 1.26E-07 1.99E-07 7.39E-07 2.43E-04 3.15E-05 I-130 4.54E-06 9.91E-06 3.98E-06 1.14E-03 1.09E-05 2.71E-05 NO DATA 1.42E-06 I-131 3.17E-05 1.40E-05 1.06E-02 3.70E-05 NO DATA - 7.56E-07
} I-132 1.21E-06 2.53E-06 8.99E-07 1.21E-04 2.82E-06 NO DATA 1.36E-06 l I-133 9.46E-06 1.37E-05 4.00E-06 2.54E-03 1.60E-05 NO DATA 1.54E-06 I-134 6.58E-07 1.34E-06 4.75E-07 3.18E-05 1.49E-06 NO DATA 9.21E-07 I-135 2.76E-06 5.43E-06 1.98E-06 4.97E-04 6.05E-06 CS-134 NO DATA 1.31E-06 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 i CS-137 3.92E-04 4.37E-04 3.25E-05 NO DATA 1.23E-04 5.09E-05 CS-138 9.53E-07 3.61E-07 5.58E-07 2.84E-07 NO DATA 2.93E-07 4.67E-08 6.26E-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 BA-141 1.12E-10 2.74E-05 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 LA-140 4.95E-07 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 CE-141 1.98E-05 4.2SE-05 1.19E-05 1.42E-06 NO DATA 3.75E-06 3.69E-04 1.54E-05 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 PR-143 7.03E-03 1.06E-04 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 p-239 2.65E-07 2.37E-08 1.34E-08 NO DATA 4.73E-08 4.25E-05 1.78E-05
- 1. 8 9 x 10 '
**Less than 10'**
l e l CLINTON-1 3-46 Rev.15-7/97j
CPS-ODCM TABLE 3.5-2 INHALATION DOSE FACTORS FOR CHILD - ( DFA ) , 3 (mrem per pCi inhaled) NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI H-3 MO DATA 3.04E-07 3.04E-07 3.04E-07 3.04E-07 3.04E-07 3.04E-07 C-14 9.07E-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-06 4.35E-06 4.35E-06 4.35E-06 4.35E-06 4.35E-06 P-32 7.04E-04 3.09E-05 2.67E-05 NO DATA NO DATA NO DATA 1.14E-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. 3 3 E-O'. 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 . 51 E- 0 6 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 CO-60 NO DATA 3.55E-06 6.12E-06 NO DATA NO DATA 1.91E-03 2.60E-05 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-ll 4.44E-ll 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-65 1.15E-05 3.06E-05 1.90E-05 NO DATA 1.93E-05 2.69E-04 4.41E-06 ZN-69 1.81E-ll 2.61E-ll 2.41E-12 NO DATA 1.58E-11 3.84E-07 2.75E-06 ER-83 NO DATA NO DATA 1.28E-07 NO DATA NO DATA NO DATA LT E-24** CR-84 NO DATA NO DATA 1.40E-07 NO DATA NO DATA NO DATA LT E-24 BR-85 NO DATA NO DATA 6.84E-09 NO DATA NO DATA NO DATA LT E-24 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 RB-89 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 K-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 DATA 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 NO DATA 4.66E-08 1.15E-08 NO DATA 1.06E-07 3.66E-05 3.42E-05 TC-997 4.81E-13 9.41E-13 1.56E-11 NO DATA 1.37E-11 2.57E-07 1.30E-06 TC-101 2.19E-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 AG-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-ll 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 CLINTON-1 3-47 Rev.15-7/97
i CPS-ODCM TABLE 3.5-2 (continued) l l INHALATION DOSE FACTORS FOR CHILD - (DFA ), 3 (mrem per pCi inhaled) NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG TE-132 GI-LLI 1.30E-07 7.36E-08 7.12E-08 8.58E-08 4.79E-07 1.02E-04 ! I-130 2.21E-06 4.43E-06 3.72E-05 2.2BE-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 I-132 5.72E-07 1.10E-06 5.07E-07 5.23E-05 1.69E-06 NO DATA I-133 4.48E-06 5.49E-06 8.65E-07 1.04E-03 l 2.08E-06 9.13E-06 NO DATA 1.48E-06 I-134 3.17E-07 5.84E-07 2.69E-07 1.37E-05 8.92E-07 NO DATA l I-135 1.33E-06 2.58E-07 2.36E-06 1.12E-06 2.14E-04 3.62E-06 NO DATA CS-134 1.76E-04 2.74E-04 1.20E-06 6.07E-05 NO DATA 8.93E-05 3.27E-05 1.04E-06 CS-136 1.76E-05 4.62E-05 3.14E-05 NO DATA 2.58E-05 3.93E-06 1.13E-06 CS-137 2.45E-04 2.23E-04 3.47E-05 CS-138 NO DATA 7.63E-05 2.81E-05 9.78E-07 1.71E-07 2.27E-07 1.50E-07 NO DATA 1.68E-07 1.84E-08 l BA-139 4.98E-10 7.29E-08 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 BA-141 5.29E-11 4.71E-04 2.75E-05 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 1A-142 3.50E-10 NO DATA 4.94E-05 6.10E-05 1.11E-10 3.49E-11 NO DATA No DATA 2.35E-06 2.05E-05
- CE-141 1.06E-05 5.28E-06 7.83E-07 NO DATA 2.31E-06 1.47E-04 1.53E-05 l CE-143 9. 89L -00 5.37E-08 7.77E-09 CE-144 NO DATA 2.26E-08 3.12E-05 3.44E-05 l
1.83E-03 5.72E-04 9.77E-05 NO DATA 3.17E-04 3.23E-03 PR-143 4.99E-06 1.50E-06 1.05E-04 2.47E-07 NO DATA 8.11E-07 1.17E-04 2.63E-05 PR-144 1.61E-11 4.99E-12 8.10E-13 ND-147 NO DATA 2.64E-12 4.23E-07 5.32E-08 2.92E-06 2.36E-06 1.84E-07 NO DATA 1.30E-06 8.87E-05 W-187 4.41E-09 2.61E-09 2.22E-05 1.17E-09 NO DATA NO DATA 1.11E-05 2.46E-05 y-239 1.26E-07 9.04E-09 6.35E-09 NO DATA 2.63E-08 1.57E-05 1.73E-05
*9.70 x 10 * * *Less than 10- ~
i l CLINTON-1 3-48 nov.15-7/97
T CPS-ODCM TABLE 3.5-3 INHALATION DOSE FACTORS FOR TEEN - ( DFA ) , (mrem per pCi inhaled) CUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI RJ- 3 NO DATA 1.59E-07 1.59E-07 1.59E-07 1.59E-07 1.59E-07 1.59E-07 d-14 3.25E-06* 6.09E-07 6.09E-07 6.09E-07 6.09E-07 6.09E-07 6.09E-07 UA-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 @R-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. 9 0 E-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 dI-63 7.25E-05 5.43E-06 2.47E-06 NO DATA NO DATA 3.84E-05 1.77E-06 QI-65 .2.73E-10 3.66E-11 1.59E-11 NO DATA NO DATA 1.17E-06 4.59E-06 CU-64 NO DATA 2.54E-10 1.06E-10 NO DATA 8.01E-10 1.39E-06 7.68E-06 DN-65 4.82E-06 1.67E-05 7.80E-06 NO DATA 1.08E-05 1.55E-04 5.83E-06 8N-69 6.04E-12 1.15E-11 8.07E-13 No DATA 7.53E-12 1.96E-07 3.56E-08 GR-Ca NO DATA No DATA 4.30E-08 NO DATA NO DATA NO DATA LT E-24** GR-Be NO DATA NO DATA 5.41E-08 NO DATA NO DATA NO DATA LT E-24 GR-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 OR-89 5.43E-05 NO DATA 1.56E-06 NO DATA NO DATA 3.02E-04 4.64E-05 SR-90 1.35E-02 NO DATA 8.35E-04 NO DATA NO DATA 2.06E-03 9.56E-05
}(-91 1.10E-08 NO DATA 4.39E-10 NO DATA NO DATA 7.59E-06 3.24E-05 dR-92 1.19E-09 NO DATA 5.08E-11 NO DATA NO DATA 3.43E-06 1.49E-05 W-90 3.73E-07 NO DATA 1.00E-08 NO DATA NO DATA 3.66E-05 6.99E-05 Yl-91m 4.63E-11 NO DATA 1.77E-12 NO DATA NO DATA 4.00E-07 3.77E-09 17-91 0.26E-05. .NO DATA 2.21E-06 NO DATA NO DATA 3.67E-04 5.11E-05 W-92 1.84E-09 NO DATA 5.36E-11 NO DATA NO DATA 3.35E-06 2.06E-05 Yt-93 1.69E-08 NO DATA 4.65E-10 NO DATA NO DATA 1.04E-05 7.24E-05 SR-95 1.82E-05 5.73E-06 3.94E-06 NO DATA 8.42E-06 3.36E-04 1.86E-05 8R-97 1.72E-08 3.40E-09 1.57E-09 NO DATA 5.15E-09 1.62E-05 7.88E-05 ]
1.2SE-06 1.21E-05 ac-95 2.32E-06 1.29E-06 7.00E-07 NO DATA 9.39E-05 MO-99 NO DATA 2.11E-08 4.03E-09 NO DATA 5.14E-08 1.92E-05 3.36E-05 TC-993 1.73E-13 4.83E-13 6.24E-12 NO DATA 7.20E-12 1.44E-07 7.66E-07 TC-101 7.40E-15 1.05E-14 1.03E-13 NO DATA 1.90E-13 8.'l4E-08 1.09E-16 RU-103 2.63E-07 NO DATA 1.12E-07 NO DATA 9.29E-07 9 , 7 '2 E-05 1.36E-05 RU-105 1.40E-10 NO DATA 5.42E-11 NO DATA le76E-10 2.27E-06 1.13E-05 B0-106 1.23E-05 NO DATA 1.55E-06 NO DATA 2.38E-05 2.01E-03 1.20E-04 AG-110m 1.73E-06 1.64E-06 9.99E-07 NO DATA 3.13E-06 8.44E-04 3.41E-05 FiE-125m 6.10E-07 2.80E-07 8.34E-08 1.75E-07 NO DATA 6.70E-05 9.38E-06 %E-127m 2.25E-06 1.02E-06 2.73E-07 5.48E-07 8.17E-06 2.07E-04 1.99E-05 $E-127 2.51E-10 1.14E-10 5.52E-11 1.77E-10 9.10E-10 1.40E-06 1.01E-05 9E-129m 1.74E-06 8.23E-07 2.81E-07 5.72E-07 6.49E-06 2.47E-04 5.06E-05 SE-129 8.87E-12 4.22E-12 2.20E-12 6.48E-12 3.32E-11 4.12E-07 2.02E-07 fsE-131m 1.23E-08 7.51E-09 5.03E-09 9.06E-09 5.49E-08 2.97E-05 7.76E-05 lTE-131 1.97E-12 1.04E-12 6.30E-13 1.55E-12 7.72E-12 2.92E-07 1.89E-09 (MT.T NTON-1, _. _ . _ _ . . 3-49 __ .. _ . _ _ . Rev.15-7/97
CPS-ODCM l TABLE 3.5-3 (continued) i i INHALATION DOSE FACTORS FOR TEEN - (DFAi ), ' (mrem per pCi inhaled) NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG TE-132 GI-LLI 4.50E-08 3.63E-08 2.74E-08 3.07E-08 2.44E-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 I-133 1.52E-06 2.56E-06 1.59E-07 7.78E-07 3.65E-04 4.49E-06 NO DATA 1.29E-06 3-134 1.11E-07 2.90E-07 1.05E-07 4.94E-06 4.58E-07 NO DATA 2.55E-09 I-135 4.62E-07 1.18E-06 4.36E-07 7.76E-05 1.86E-06 NO DATA 8.69E-07 CS-134 6.28E-05 1.41E-04 6.86E-05 NO DATA 4.69E-05 CS-136 1.83E-05 1.22E-06 6.44E-06 2.42E-05 1.71E-05 NO DATA 1.38E-05 2.22E-06 CS-137 1.36E-06 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 8.28E-08 BA-139 1.67E-10 NO DATA 9.84E-09 3.38E-11 l 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 BA-141 2.54E-04 2.86E-05 1.78E-11 1.32E-14 5.93E-13 NO DATA 1.23E-14 4.11E-07 l BA-142 4.62E-12 4.63E-15 9.33E-14 2.84E-13 NO DATA 3.92E-15 2.39E-07 5.99E-20 LA-140 5.99E-08 2.95E-08 7.82E-09 NO DATA NO DATA 2.68E-05 LA-142 1.20E-10 5.31E-11 6.09E-05 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 CE-143 1.llE-06 7.67E-05 1.58E-05 3.32E-08 2.42E-08 2.70E-09 NO DATA 1.08E-08 1.63E-05 CE-144 6.11E-04 2.53E-04 3.19E-05 3.28E-05 NO DATA 1.51E-04 1.67E-03 1.08E-04 PR-143 1.67E-06 6.64E-07 8.28E-08 NO DATA 3.86E-07 6.04E-05 2.67E-05 l PR-144 5.37E-12 2.20E-12 2.72E-13 ND-147 NO DATA 1.26E 2.19E-07 2.94E-14 l 9.83E-07 1.07E-06 6.41E-08 NO DATA 6.28E-07 4.65E-05 ! W-187 1.50E-09 1.22E-09 2.28E-05 4.29E-10 NO DATA NO DATA 5.92E-06 2.21E-05 f-239 4.23E-08 3.99E-09 2.21E-09 NO DATA 1.25E-08 8.11E-06 1.65E-05 03.52 x 10-" 00Less than 10-** l i l l CLINTON-1 3-50 Rev .15-7 / 97j
i CPS-ODCM l TABL,E 3.5-4 1 1 INHALATION DOSE FACTORS FOR ADULT - ( D FAi ) , (mrem per pCi inhaled) NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI H-3 NO DATA 1.58E-07 1.58E-07 1.58E-07 1.58E-07 1.58E-07 1.58E-07 C-14 2.27E-06* 4.26E-07 4.26E-07 4.26E-07 4.26E-07 4.26E-07 4.26E-07 NA-24 1.28E-06 1.28E-06 1.28E-06 1.28E-06 1.28E-06 1. 2 8 E- 0 6 1.28E-06 P-32 1.65E-04 9.64E-06 6.26E-06 NO DATA NO DATA NO DATA 1.08E-05 CR-51 NO DATA NO DATA 1.25E-08 7.44E-09 2.85E-09 1.80E-06 4.15E-07 MN-54 NO DATA 4.95E-06 7.87E-07 NO DATA 1.23E-06 1.75E-04 9.67E-06 MN-56 NO DATA 1.55E-10 2.29E-11 NO DATA 1.63E-10 1.18E-06 2.53E-06 FE-55 3.07E-06 2.12E-06 4.93E-07 NO DATA NO DATA 9.01E-06 7.54E-07 FE-59 1.47E-06 3.47E-06 1.32E-06 NO DATA NO DATA 1.27E-04 2.35E-05 CO-58 NO DATA 1.98E-07 2.59E-07 NO DATA NO DATA 1.16E-04 1.33E-05 CO-60 NO DATA 1.44E-06 1.85E-06 NO DATA NO DATA 7.46E-04 3.56E-05 NI-63 5.40E-05 3.93E-06 1.81E-06 NO DATA NO DATA 2.23E-05 1.67E-06 NI-65 1.92E-10 2.62E-ll 1.14E-11 NO DATA NO DATA 7.00E-07 1.54E-06 CU-64 NO DATA 1.83E-10 7.69E-11 NO DATA 5.78E-10 8.48E-07 6.12E-06 ZN-65 4.05E-06 1.29E-05 5.82E-06 NO DATA 8.62E-06 1.08E-04 6.68E-06 l ZN-69 4.23E-12 8.14E-12 5.65E-13 NO DATA 5.27E-12 1.15E-07 2.04E09 l CR-83 NO DATA NO DATA 3.01E-08 NO DATA NO DATA NO DATA 2.90E-08 l*R-84 I NO DATA NO DATA 3.91E-08 NO DATA NO DATA NO DATA 2.05E-13 i LR-85 NO DATA NO DATA 1.60E-09 NO DATA NO DATA NO DATA LT E-24** I RB-86 NO DATA 1.69E-05 7.37E-06 NO DATA NO DATA NO DATA 2.08E-06 RB-88 l NO DATA 4.84E-08 2.41E-08 NO DATA NO DATA NO DATA 4.18E-19 i RB-89 NO DATA 3.20E-08 2.12E-08 NO DATA NO DATA NO DATA 1.16E-21 SR-89 3.80E-05 NO DATA 1.09E-06 NO DATA NO DATA 1.75E-04 4.37E-05 SR-90 1.24E-02 NO DATA 7.62E-04 NO DATA NO DATA 1.20E-03 9.02E-05 p-91 7.74E-09 NO DATA 3.13E-10 NO DATA NO DATA 4. 5 6E-06 2.39E-05 .m-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-09 NO DATA 3.71E-09 9.84E-06 6.54E-05 N2-95 1.76E-06 9.77E-07 5.26E-07 NO DATA 9.67E-07 6.31E-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 AG-110m 1.35E-06 1.25E-06 7. 4 ~3 E-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.llE-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 1.39E-12 7.44E-13 4.49E-13 1.17E-12 5.46E-12 1.74E-07 2.30E-09 CLINTON-1 3-51 Rev.15-7/97
CPS-ODCM TABLE 3.5-4 ( con t. i n ued ) l INHALATION DOSE FACTORS FOR ADULT - (DFA ), i (mrem per pCi inhaled) NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI TE-132 3.25E-00 2.69E-08 2,02E-08 2.37E-08 1.82E-07 3.60E-05 6.37E-05 I-130 5.72E-07 1.68E-06 6.60E-07 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 I-132 1.45E-07 4.07E-07 1.45E-07 1.43E-05 6.4BE-07 NO DATA 5.08E-08 ~i I-133 1.08E-06 1.85E-06 5.65E-07 2.69E-04 3.23E-06 NO DATA 1.11E-06 I-134 8.05E-08 2.16E-07 7.69E-08 3.73E-06 3.44E-07 NO DATA 1.26E-10 I-135 3.35E-07 0.73E-07 3.21E-07 5.60E-05 NO DATA CS-134 1.39E-06 6.56E-07 4.66E-05 1.06E-04 9.10E-05 NO DATA 3.59E-05 1.22E-05 1.30E-06 CS-136 4.88E-06 1.83E-05 1.38E-05 NO DATA 1.07E-05 1.50E-06 1.46E-06 CS-137 5.98E-05 7.76E-05 5.35E-05 NO DATA CS-138 2.78E-05 9.40E-06 1.05E-06 4.14E-08 7.76E-08 4.05E-08 NO DATA 6.00E-08 6.07E-09 2.33E-13 BA-139 1.17E-10 8.32E-14 3.42E-12 NO DATA 7.78E-14 4.70E-07 1.12E-07 BA-140 4.88E-06 6.13E-09 3.21E-07 NO DATA 1.59E-04 BA-141 2.09E-09 2.73E-05 1.25E-11 9.41E-15 4.20E-13 NO DATA 8.75E-15 2.42E-07 1.45E-17 BA-142 3.29E-12 3.38E-15 2.07E-13 NO DATA 1.49E-07 IA-140 2.86E-15 1.96E-26 4.30E-08 2.17E-08 5.73E-09 NO DATA NO DATA 1.70E-05 5.73E-05 LA-142 8.54E-11 3.88E-11 9.65E-12 NO DATA NO DATA 7.91E-07 CE-141 2.64E-07 2.49E-06 1.69E-06 1.91E-07 NO DATA 7.83E-07 4.52E-05 1.50E-05 CE-143 2.33E-08 1.72E-08 1.91E-09 NO DATA 7.60E-09 9.97E-06 2.83E-05 CE-144 4.29E-04 1.79E-04 2.30E-05 NO DATA 1.06E-04 9.72E-04 PR-143 1.17E-06 1.02E-04 4.69E-07 5.80E-08 NO DATA 2.70E-07 3.51E-05 2.50E-05 PR-144 3.76E-12 1.56E-12 1.91E-13 NO DATA 8.81E-13 1.27E-07 2.69E-18 ND-147 6.59E-07 7.62E-07 4.56E-08 NO DATA 4.45E-07 2.76E-05 2.16E-05 W-187 1.06E-09 8.85E-10 3.10E-10 NO DATA NO DATA 3.63E-06 1.94E-05 NP-239 2.87E-08 2.82E-09 1.55E-09 NO DATA 8.75E-09 4.70E-06 1.49E-05 02.27 x 10"
. COLess than 10-"
1 CLINTON-1 3-52 Rev.15 -7 / 97
CPS-ODCM TABLE 3.5-5 GROUND PLANE DOSE FACTORS - DFG 3 (mrem /hr per pCi/m') ELEMENT TOTAL BODY SKIN 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 ! Mn-56 1.10E-08 1.30E-08 i Fe-55 0.0 0.0 l Fe-59 8.00E-09 9.40E-09 l 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-64 1.50E-09 1.70E-09 Zn-65 4.00E-09 4.60E-09 j Zn-69 0.0 0.0 1 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 kb-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-09 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 _Zr-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 Ag-110m 1.80E-08 2.10E-08 l CLINTON-1 3-53 Rev.15-7/97
l CPS-ODCM l TABLE 3.5-5 (Continued) f GROUND PLANE DOSE FACTORS - DFG 3 (mrem /hr per pCi/m") ELEMENT TOTAL BODY SKIN 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 l Te-129 7.10E-10 8.40E-10 i Te-131m 8.40E-09 9.90E-09 l 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 l I-135 1.20E-08 1.40E-08 l Cs-134 1.20E-08 1.40E-08 l Cn-136 1.50E-08 1.70E-08 ( Cs-137 4.20E-09 4.90E-09 Cs-138 2.10E-08 2.40E-08 Ba-139 2.40E-09 2.70E-09 Ba-140 2.10E-09 2.40E-09 Sa-141 4.30E-09 4.90E-09 l Ba-142 , 7.90E-09 9.00E-09 l L2-140 1.50E-08 1.70E-08 Lo-142 1.50E-08 1.80E-08 Co-141 5.50E-10 6.20E-10 l Co-143 2.20E-09 2.50E-09 Cc-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 W-187 3.10E-09 3.60E-09 Np-239 9.50E-10 1.10E-09
- 2. 50 X 10-"
CLINTON-1 3-54 Rev.15-7/97
CPS-ODCM TABLE 3.5-6 INGESTION DOSE FACTORS FOR INFANT - (DFLi ), (mrem per pCi ingested) NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI H-3 NO DATA 3.00E-07 3.08E-07 3.08E-07 3.08E-07 3.08E-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 1.01E-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 f' 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 7.03-07 NO 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 2.57E-05 DI-63 6.34E-04 3.92E-05 2.20E-05 NO DATA NO DATA NO DATA 1.95E-06 QI-65 4.70E-06 5.32E-07 2.42E-07 NO DATA NO DATA NO DATA 4.05E-05 4U-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 EN-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 NO DATA NO DATA LT E-24** CR-84 NO DATA NO DATA 3.82E-07 NO DATA NO DATA NO DATA LT E-24 ER-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 RB-89 NO DATA 2.86E-07 1.97E-07 NO DATA NO DATA NO DATA 9.74E-08 OR-89 2.51E-03 NO DATA 7.20E-05 NO DATA NO DATA NO DATA 5.16E-05 OR-90 1.85E-02 NO DATA 4.71E-03 NO DATA NO DATA NO DATA 2.31E-04 OR-91 5.00E-05 NO DATA 1.81E-06 NO DATA NO DATA NO DATA 5.92E-05 JR-92 1.92E-05 NO DATA 7.13E-07 NO DATA NO DATA NO DATA 2.07E-04 . W-90 8.69E-08 NO DATA 2.33E-09 NO DATA NO DATA NO DATA 1.20E-04 l W-913 8.10E-10 NO DATA 2.76E-11 NO DATA NO DATA NO DATA 2.70E-06 W-91 1.13E-06 NO DATA 3.01E-08 NO DATA NO DATA NO DATA 8.10E-05 W-92 7.65E-09 NO DATA 2.15E-10 NO DATA NO DATA NO DATA 1.46E-04 8-93 2.43E-08 NO DATA 6.62E-10 NO DATA NO DATA NO DATA 1.92E-04 GR-95 2.06E-07 5.02E-08 3.56E-08 NO DATA 5.41E-08 NO DATA 2.50E-05 BR-97 1.48E-08 2.54E-09 1.16E-09 NO DATA 2.56E-09 NO DATA 1.62E-04 !1B-95 4.20E-08 1.73E-08 1.00E-08 NO DATA 1.24E-08 NO DATA 1.46E-05 MO-99 NO DATA 3.40E-05 6.63E-06 NO DATA 5.0BE-05 NO DATA 1.12E-05 TC-99m 1.92E-09 3.96E-09 5.10E-08 NO DATA 4.26E-08 2.07E-09 1.15E-06 TC-101 2.27E-09 2.86E-09 2.83E-08 NO DATA 3.40E-08 1.56E-09 4.86E-07 RU-103 1.40E-06 NO DATA 4.95E-07 NO DATA 3.0BE-06 NO DATA 1.80E-05 i RU-105 1.36E-07 NO DATA 4.58E-08 NO DATA 1.00E-06 NO DATA 5.41E-05 l RU-106 . 2.41E-05 NO DATA 3.01E-06 NO DATA 2.85E-05 NO DATA 1.83E-04 AG-110m 9.96E-07 7.27E-07 '4.81E-07 NO DATA 1.04E-06 NO DATA 3.77E-05 EE-1251 2.33E-05 7.79E-06 3.15E-06 7.84E-06 NO DATA NO DATA 1.11E-05 TE-127m 5.85E-05 1.94E-05 7.08E-06 1.69E-05 1.44E-04 NO DATA 2.36E-05 l UE-127 1.00E-06 3.35E-07 2.15E-07 8.14E-07 2.44E-06 NO DATA 2.10E-05 l DE-129m 1.00E-04 3.43E-05 1.54E-05 3.84E-05 2.50E-04 NO DATA 5.97E-05 TE-129 2.84E-07 9.79E-08 6.63E-08 2.38E-07 7.07E-07 NO. DATA 2.27E-05 EE-131n 1.52E-05 6.12E-06 5.05E-06 1.24E-05 4.21E-05 NO DATA 1.03E-04 TE-131 1.76E-07 6.50E-08 4.94E-08 1.57E-07 4.50E-07 NO DATA 7.11E-06 I i $LINTON-1 3-55 Rev.15-7/97 j
i CPS-ODCM l TABLE 3.5-6 (continued) TNGESTION DOSE FACTORS FOR INFANT - ( DFL ) , i (mrem per pCi ingested) NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI TE-132 2.08E-05 1.03E-05 9.61E-06 1.52E-05 6.44E-05 NO DATA 3.81E-05 l I-130 6.00E-06 1.32E-05 5.30E-06 1.48E-03 1.45E-05 NO DATA 2.83E-06 I-131 3.59E-05 4.23E-05 1.86E-05 1.39E-02 4.94E-05 NO DATA 1.51E-06 I-132 1.66E-06 3.37E-06 1.20E-06 1.58E-04 3.76E-06 NO DATA 2.73E-06 I-133 1.25E-05 1.82E-05 5.33E-06 3.31E-03 2.14E-05 NO DATA 3.08E-06 I-134 8.69E-07 1.78E-06 6.33E-07 4.15E-05 1.99E-06 NO DATA 1.84E-06 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 l 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 l BA-139 8.81E-07 5.84E-10 2.55E-08 NO DATA 3.51E-10 3.54E-10 5.58E-05 ' BA-140 1.71E-04 1.71E-07 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 LA-140 2.llE-08 8.32E-09 2.14E-09 NO DATA NO DATA NO DATA 9.77E-05 . 1A-142 1.10E-09 4.04E-10 9.67E-11 NO DATA NO DATA NO DATA 6.86E-05 l CE-141 7.87E-08 4.80E-08 5.65E-09 NO DATA 1.48E-08 NO DATA 2.48E 05 l 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-10 1.06E-10 1.38E-11 NO DATA 3.84E-11 NO DATA 4.93E-06 i 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 NO DATA NO DATA NO DATA 3.69E-05 NP-239 1.11E-08 9.93E-10 5.61E-10 NO DATA 1.9BE-09 NO DATA 2.87E-05
*2.37 x 10" * *Less than 10-"
CLINTON-1 3-56 n ,,,, , n 7 / o7 '
I l CPS-ODCM TABLE 3.S-7 INGESTION DOSE FACTORS FOR CHILD - ( D FL )i , (mrem per pCi ingested) NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI H-3 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-05 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 2.85E-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-05 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-63 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 ZN-69 4.38E-08 6.33E-08 5.85E-09 NO DATA 3.84E-08 NO DATA 3.99E-06 CR-83 NO DATA NO DATA 1.71E-07 NO DATA NO DATA NO DATA LT E-24** BR-84 NO DATA NO DATA 1.98E-07 NO DATA NO DATA NO DATA LT E-2.4 LR-85 NO DATA NO DATA 9.12E-09 NO DATA NO DATA NO DATA LT E-24 RB-86 NO DATA 6.70E-05 4.12E-05 NO DATA NO DATA NO DATA 4.31E-06 RB-88 NO DATA 1.90E-07 1.32E-07 NO DATA NO DATA NO DATA 9.32E-09 RB-89 NO DATA 1.17E-07 1.04E-07 NO DATA NO DATA NO DATA 1.02E-09 SR-89 1.32E-03 NO DATA 3.77E-05 NO DATA NO DATA NO DATA 5.11E-05 SR-90 1.70E-02 NO DATA 4.31E-03 NO DATA NO DATA NO DATA 2.29E-04 SR-91 2.40E-05 NO DATA 9.06E-07 NO DATA NO DATA NO DATA 5.30E-05 AR-92 9.03E-06 NO DATA 3.62E-07 NO DATA NO DATA NO DATA 1.71E-04 Y-90 4.11E-08 NO DATA 1.10E-09 NO DATA NO DATA NO DATA 1.17E-04 Y-91m 3.82E-10 NO DATA 1.39E-11 NO DATA NO DATA NO DATA 7.48E-07 Y-91 - 6.02E-07 NO DATA 1.61E-08 NO DATA NO DATA NO DATA 8.02E-05 Y-92 3.60E-09 NO DATA 1.03E-10 NO DATA NO DATA NO DATA 1.04E-04 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 6.26E-09 NO DATA 8.23E-09 NO DATA 1.62E-05 l HO-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 l 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 5.39E-07 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 l 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 ('T T M'TY wt_ 1 ~4 - 4 *7 Dmr 1 E *7 / 4 *7
\
CPS-ODCM TABLE 3.5-7 (continued) INGESTION DOSE FACTORS FOR CHILD - (DFLi ), (mrem per pCi ingested) NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI TE-132 1.01E-05 4.47E-06 5.40E-06 6.51E-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 9.83E-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 1.36E-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 I-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 CS-136 2.35E-05 6.46E-05 4.18E-05 NO DATA 3.44E-05 5.13E-06 2.27E-06 CS-137 3.27E-04 3.13E-04 4.62E-05 NO DATA 1.02E-04 3.67E-05 1.96E-06 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 BA-140 8.31E-05 7.28E-08 4.85E-06 NO DATA 2.37E-08 4.34E-08 4.21E-05 BA-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-ll 1.14E-09 LA-140 1.01E-68 3.53E-09 1.10E-09 NO DATA NO DATA NO DATA 9.84E-05 IA-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 1 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 ND-147 2.79E-08 2.26E-08 1.75E-09 NO DATA 1.24E-08 NO DATA 3.58E-05 W-187 4.29E-07 2.54E-07 1.14E-07 NO DATA NO DATA NO DATA 3.57E-05 WP-239 5.25E-09 3.77E-10 2.65E-10 NO DATA 1.09E-09 NO DATA 2.79E-05
)
01.21 x 10 " 00Less than 10-*' i l CLINTON-1 3-58 Rev.15 '7/97
l CPS-ODCM TABLE 3.5-8 INGESTION DOSE FACTORS FOR TEEN - (DFLi ) . (mrem per pCi ingested) NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI H-3 NO DATA 1.06E-07 1.06E-07 1.06E-07 1.06E-07 1.06E-07 1.06E-07 j 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 l 2.30E-06 2.30E-06 P-32 2.76E-04 1.71E-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-09 6.05E-07 MN-54 NO DATA 5.90E-06 1.17E-06 NO DATA 1.76E-06 NO DATA 1.21E-05 l HN-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 6.2SE-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 I 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 7.49E-07 9.57E-08 4.36E-08 NO DATA NO DATA NO DATA 5.19E-06 CU-64 NO DATA 1.15E-07 5.41E-08 NO DATA 2.91E-07 NO DATA 8.92E-06 ZN-65 5.76E-06 2.00E-05 9.33E-06 NO DATA 1.20E-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 1 R-91 8.07E-06 NO DATA 3.21E-07 NO DATA NO DATA NO DATA 3.66E-05
.%R-92 3.05E-06 NO DATA 1.30E-07 NO DATA NO DATA NO DATA 7.77E-05 Y-90 1.37E-08 NO DATA 3.69E-10 NO DATA NO DATA NO DATA 1.13E-04 Y-91m 1.29E-10 NO DATA 4.93E-12 NO DATA NO DATA NO DATA 6.09E-09 Y-91 2.01E-07 NO DATA 5.39E-09 NO DATA NO DATA NO DATA 8.24E-05 Y-92 1.21E-09 NO DATA 3.50E-11 NO DATA NO DATA NO DATA 3.32E-05 Y-93 3.83E-09 NO DATA 1.05E-10 NO DATA NO DATA NO DATA 1.17E-04 ZR-95 4.12E-08 1.30E-08 8.94E-09 NO DATA 1.91E-08 NO DATA 3.00E-05 ER-97 2.37E-09 4.69E-10 2.16E-10 NO DATA 7.llE-10 NO DATA 1.27E-04 N2-95 0.22E-09 4.56E-09 2.51E-09 No DATA 4.42E-09 NO DATA ~ 1.95E-05 MO-99 NO DATA 6.03E-06 1.15E-06 No DATA 1.38E-05 NO DATA 1.08E-05 TC-993 3.32E-10 9.26E-10 1.20E-08 NO DATA 1.38E-08 5.14E-10 6.08E-07 TC-101 3.60E-10 5.12E-10 5.03E-09 NO DATA 9.26E-03 3.12E-10 8.75E-17 RU-103 2.55E-07 NO DATA 1.09E-07 NO DATA 8.99E-07 NO DATA 2.13E-05 RU-105 2.18E-08 NO DATA 8.46E-09 NO DATA 2.75E-07 NO DATA 1.76E-05 RU-106 3.92E-06 NO DATA 4.94E-07 NO DATA 7.56E-06 NO DATA 1.88E-04 AG-110m 2.058-07 1.94E-07 1.18E-07 NO DATA 3.70E-07 NO DATA 5.45E-05 TE-125m 3.83E-06 1.3BE-06 5.12E-07 1.07E-06 NO DATA NO DATA 1.13E-05 TE-127a 9.67E-06 3.43E-06 1.15E-06 2.30E-06 3.92E-05 NO DATA 2.41E-05 TE-127 1.58E-07 5.60E-08 3.40E-08 1.09E-07 6.40E-07 NO DATA 1.22E-05 TE-1293 1.63E-05 6.05E-06 2.58E-06 5.26E-06 6.82E-05 NO DATA 6.12E-05 TE-129 4.48E-08 1.67E-08 1.09E-08 3.20E-08 1.88E-07 NO DATA 2.45E-07 TE-131m 2.44E-06 1.17E-06 9.76E-07 1.76E-06 1.22E-05 NO DATA 9.39E-05 TE-131 2.79E-08 1.15E-08 8.72E-09 2.15E-00 1.22E-07 NO DATA 2.29E-09 CLINTON-1 3-59 Rev.15-7/97
CPS-ODCM TABLE 3.5-8 (continued) INGESTION DOSE FACTORS FOR TEEN - (DFL ), 3 (mrem per pCi ingested) NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI TE-132 3.49E-06 2.21E-06 2.08E-06 2.33E-06 2.12E-05 NO DATA 7.00E-05 I-130 1.03E-06 2.98E-06 1.19E-06 2.43E-04 4.59E-06 NO DATA 2.29E-06 I-131 5.85E-06 8.19E-06 4.40E-06 2.39E-03 1.41E-05 NO DATA 1.62E-06 I-132 2.79E-07 7.30E-07 2.62E-07 2.46E-05 1.15E-06 NO DATA 3.18E-07 I-133 2.01E-06 3.41E-06 1.04E-06 4.76E-04 5.98E-06 NO DATA 2.58E-06 I-134 1.46E-07 3.87E-07 1.39E-07 6. 4 5E- 06 6.10E-07 NO DATA 5.10E-09 Z-135 6.10E-07 1.57E-06 5.82E-07 1.01E-04 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 4.05E-09 NO DATA 9.22E-11 6.74E-11 1.24E-06 BA-140 2.84E-05 3.48E-08 1.83E-06 NO DATA 1.18E-08 2.34E-08 4.30E-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 2.428-06 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 PR-143 NO DATA 1.75E-04 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 W-187 NO DATA 3.68E-05 1.46E-07 1.19E-07 4.17E-08 NO DATA NO DATA NO DATA 3.22E-05
}P-239 1.76E-09 1.66E-10 9.22E-11 NO DATA 5.21E-10 NO DATA 2.67E-05 04.06 x 10*
00Less than 10-** CLINTON-1 3-60 priv .1 s-7 / 97
1 l l l CPS-ODCM TABLE 3.5-9 INGESTION DOSE ' FACTORS FOR ADULT - (DFLi ), ! (mrem per pCi ingested) 'NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI !H-3 NO DATA 1.05E-07 1.05E-07 1.05E-07 1.05E-07 1.05E-07 1.05E-07 lC-14 2.84E-06* 5.68E-07 5.68E-07 5.68E-07 5.68E-07 5.68E-07 5.68E-07 'NA-34 1.70E-06 1.70E-06 1.70E-06 1.70E-06 1.70E-06 1.70E-06 1.70E-06 P-33 1.93E-04 1.20E-05 7.46E-06 NO DATA NO DATA NO DATA 2.17E-05 lCR-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 lCO-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 NO DATA 8.33E-08 3.91E-08 NO DATA 2.10E-07 NO DATA '7.10E-06
- EN-65 4. bee-06 1.54E-05 6.96E-06 NO DATA 1.03E-05 NO DATA 9.70E-06 EN-69 1.03E-08 1.97E-08 1.37E-09 NO DATA 1.28E-08 N0 DATA 2.96E-09 MR-83 NO DATA NO DATA 4.02E-08 NO DATA NO DATA NO DATA 5.79E-08
!ER-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** ,
iRB-86 NO DATA 2.11E-05 9.83E-06 NO DATA NO DATA NO DATA 4.16E-06 i
- 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 2.33E-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
- SR-91 5.67E-06 NO DATA 2.29E-07 NO DATA NO DATA NO DATA 2.70E-05 lJR-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
- Y-91m 9.09E-11 NO DATA 3.52E-12 NO DATA NO DATA NO DATA 2.67E-10
!Y-91 1.41E-07 NO DATA 3.77E-09 NO DATA NO DATA NO DATA 7.76E-05
- Y-92 8.45E-10 NO DATA 2.47E-11 NO DATA NO DATA NO DATA 1.48E-05
- Y-93 2.68E-09 NO DATA 7.40E-11 NO DATA NO DATA NO DATA 8.50E-05 ER-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 1.05E-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 NO DATA 9.99E-06 TC-99m 2.47E-10 6.98E-10 8.89E-09 NO DATA 1.06E-08 3.42E-10 4.13E-07 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 i
RU-106 2.75E-06 NO DATA 3.48E-07 NO DATA 5.31E-06 NO DATA 1.78E-04 'AG-110m 1.60E-07 1.48E-07 8.79E-08 NO DATA 2.91E-07 NO DATA 6.04E-05 EE-125m 2.68E-06 9.71E-07 3.59E-07 8.06E-07 1.09E-05 NO DATA 1.07E-05 lnE-127m 6.77E-06 2.42E-06 8.25E-07 1.73E-06 2.75E-05 NO DATA 2.27E-05 TFE-127 1.10E-07 3.95E-08 2.38E-08 8.15E-08 4.48E-07 NO DATA 8.68E-06 NIE-129m 1.15E-05 4.29E-06 1.82E-06 3.95E-06 4.80E-05 NO DATA 5.79E-05 $E-129 3.14E-08 1.18E-08 7.65E-09 2.41E-08 1.32E-07 NO. DATA 2.37E-08 EE-131m 1.73E-06 8.46E-07 7.05E-07 1.34E-06 8.57E-06 NO DATA 8.40E-05 EFE-131 1.97E-08 8.23E-09 6.22E-09 1.62E-08 8.63E-08 NO DATA 2.79E-09 l @LINTON-1 3-61 Rev.15-7/97
CPS-ODCM TABLE 3.5-9 (continued) INGESTION DOSE FACTORS FOR ADULT - (DFL i), (mrem per pCi ingested) NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI 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 I-131 4.16E-06 5.95E-06 3.41E-06 1.95E-03 1.02E-05 NO DATA 1.57E-06 I-132 2.03E-07 5.43E-07 1.90E-07 1.90E-05 8.65E-07 NO DATA 1.02E-07 I-133 1.42E-06 2.47E-06 7.53E-07 3.63E-04 4.31E-06 NO DATA 2.22E-06 I-134 1.06E-07 2.88E-07 1.03E-07 4.99E-06 4.58E-07 NO DATA 2.51E-10 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-08 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 3.56E-11 1.59E-09 NO DATA 3.31E-11 2.02E-11 2.22E-17 BA-142 2.13E-06 2.19E-11 1.34E-09 HO 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 IA-142 1.28E-10 5.82E-11 1.45E-11 NO DATA NO DATA NO DATA 4.2SE-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 1.2SE-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 6.45E-11 NO DATA 3.65E-10 NO DATA 2.40E-05
} *2.84 x 10-" * *Less than 10-*'
CLINTON-1 3-62 Rev.15-7/97
CPS-ODCM TABLE 3.5-10 INPUT PARAMETERS FOR CALCULATING R',o ' Parameter Value Table
- Or(kg/ day) 50 for cow E-3 i 6 for goat U,p (liters /yr) - Infant 330 E-5
- Child 330 E-5 Teen 400 E-5 Adult 310 E-5 Yp (kg/m*) 0.7 E-15 Y, ( kg/m') 2.0 E-15 l F.(days / liter) Each stable element for cow E-1 Each stable element for goat E-2, r(dimensionless) 1.0 for radioiodine E-15 0.2 for.particulates E-15 )
tr(seconds) 1,73 x 10*(:2 days) E-15 t h(seconds) 7.78 x 10'(90 days) E-15
- f. (dimensionless) 1.0 for cow NUREG -
1.0 for goat 0133 Section 5.3.1.3 f p(dimsnsionless) 1.0 for cow NUREG - 1.0 for goat 0133 Section , 5.3.1.3
- of Regulatory Guide 1.109 unless otherwise stated l
1 l l LINTON-1 3-63 Rev.15-7/97
CPS-ODCM TABLE 3.5-11 INPUT PARAMETERS FOR CALCULATING R"33 Parameter Value Table
- U,p(liters /yr) -
Infant 0 E-5
- Child 41 E-5
- Teen 65 E-5
- Adult 110 E-5 Fr (days /kg) Each stable element E-1 t.(seconds) 1.73E+06 (20 days) E-15 tn(seconds) 7.78E+06 (90 days) E-15 Yp (Pg/m*) O.7 E-15 Y. ( kg/m*) 2.0 E-15 r(dimensionless) 1.0 for radiciodine E-15 0.2 for particulates E-15 Or (kg/ day) 50 E-3 1
*of Regulatory Guide 1.109 I
CLINTON-1 3-64 Rev.15-7/97 L- . _ _ _ _ _ _ _ _ _____ _ . .
l l i l CPS-ODCM TABLE 3.5-12 j i INPUT PARAMETERS FOR CALCULATING R*,y 4 l Parameter Value Table
- l U '. (kg/yr) - Infant 0 E-5 j
- Child 26 E-5 l
- Teen 42 E-5 l
- Adult 64 E-5 !
8 lU . (kg/yr) - Infant 0 E-5
- Child 520 E-5 4
- Teen 630 E-5
- Adult 520 E-5 l
lft (dimensionless) 1.0 E-15 f, (dimensionless) 0.76 E-15 ; ltt (seconds) 8.6 x 10' (1 day) E-15 ltn (ssconds) 5.18 x 10' (60 days) E-15 (Y, (kg/m*) 2.0 E-15 l l*of Regulatory Guide 1.109 - i I j l i l I l l l \ ( CT.T NTON-1 3-65 Rev.15-7/97
I CPS-ODCM TABLE 3.5-13 j
)
INHALATION PATHWAY FACTORS - R' g (INFANT) j (mrem /yr per pCi/m') ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE H-3 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 5.31E403 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 1.28E404 3.57E+02 MN-54 NO DATA 2.53E+04 4.98E+03 NO DATA 4. 98E4 03 1.00E+06 7.06E+03 MN-56 NO DATA 1.54E+00 2.21E-01 NO DATA 1.10E+00 1.25E+04 7.17E+04 FE-55 1.97E+04 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 2.40E+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 1.18E+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 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. 74 E-01L NO DATA 3.98E+00 9.30E+03 1.50E+04 ZN-65 1.93E+04 6.26E+04 3.11E'd4 NO DATA 3.25E+04 6.47E+05 5.14E+04 ZN-69 5.39E-02 9.67E-02 7718E-03 NO DATA 4.02E-02 1.47E+03 1.32E+04 BR-83 NO DATA NO DATA 3.81E+02 NO DATA NO DATA NO DATA LT1. 4 E-15 *
- CR-84 NO DATA NO DATA 4.00E+02 NO DATA NO DATA NO DATA LT1.4E-15 ER-85 NO DATA NO DATA 2.04E+01 NO DATA NO DATA NO DATA LT1.4E-15 RB-86 NO DATA 1.90E+05 8.82E+04 NO DATA NO DATA NO DATA 3.04E+03 RB-88 NO DATA 5.57E+02 2.87E+02 NO DATA NO DATA NO DATA 3.39E+02 RB-89 NO DATA 3.21E+02 2.06E+02 NO DATA NO DATA NO DATA 6.82E+01 SR-89 3.98E+05 NO DATA 1.14E+04 NO DATA NO DATA 2.03E+06 6.40E+04
$R-90 4.09E+07 NO DATA 2.59E+06 NO DATA NO DATA 1.12E+07 1.31E+05
.BR-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 Z R 1.15E+05 2.79E+04 2.03E+04 NO DATA 3.11E+04 1.75E+06 2.17E+04 ZR-97 1.50E+02 2.56E+01 1.17E+01 NO DATA 2.59E+01 1.10E+05' 1.40E+05 NB-95 1.57E+04 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 TC-101 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 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 CLINTON-1 3-66 Rev.15-7p7
CPS-ODCM TABLE 3.5-13 (continued) INHALATION PATHWAY FACTORS - R*m (INFANT) (mrem /yr per pCi/m') ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE TE-132 3.72E+02 2.37E+02 1.76E+02 2.79E+02 1.03E+03 3.40E+05 4.41E+04 I I-130 6.39E+03 1.39E+04 5.57E+03 1.60E+06 1.53E+04 NO DATA 1.99E+C3 I-131 3.79E+04 4.44E+04 1.96E+04 1.48E+07 5.18E+04 NO DATA 1.06E+03 I-132 1.69E+03 3.54E+03 1.26E+03 1.69E+05 3.95E+03 NO DATA 1.90E+03 I-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 1.88E403 6.65E+02 4.45E+04 2.09E+03 NO DATA 1.29E+03 I-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-138 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 BA-142 3.98E-02 3.30E-05 1.96E-03 NO DATA 1.90E-05 1.55E+03 6.93E+02 IA-140 5.05E+02 2.00E+02 5.15E+01 NO DATA NO DATA 1.68E+05 8.48E+04 IA-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 PR-144 4.79E-02 1.85E-02 2.41E-03 NO DATA 6.72E-03 1.61E+03 4.28E+03 ND-147 7.94E+03 8.13E+03 5.00E+02 NO DATA 3.15E+03 3.22E+05 3.12E+04 y-187 1.30E+01 9.02E+00 3.12E+00 NO DATA NO DATA 3.96E+04 3.56E+04 LP-239 3.71E+02 3.32E+01 1.88E+01 NO DATA 6.62E+01 5.95E+04 2.49E+04 6 6. 4 7 x 10'
** Loss than 1.40 x 10*
l l l J I J CLINTON-1 3-67 Rev.15-7/97 l
3dS-OGDW lvala E*9-I& INHV1V1 ION dVIHMVA 3V31 OHS - B % )OHI7G(
)mlam/42 dal iT O T / m (
OHDVN* OON3 1'IA3H 1*GOGA 1HAHOIG NIGN3A I'nND DI-ITI IS01Od3 H-C NO GVIV I*I23+0E, I*123+0E I*I23+0E I*I23+0E I*I23+0E I*I23+0C 3-IP E'G83+07 9*LE3+0E 9*LE3+0E 9*LE3+0E 9*LE3+0E 9'LE3+0E 9*LE3+0E NV-ZP I'913+0t I'9I3+0t I*9I3+OP I'913+0t I'9I3+ot I'9I3+ot I'9I3+09 d-CZ 2*903+09 I*It3+OS- 6*8L3+09 NO GVIV NO GY1V NO GVIV t*ZI3+OP 3H-SI NO QVIV NO GV1V I*SP3+02 8*S>3+01 2*PE3+OI I*L03+0# I*083+0E HN-SP NO GV1Y t*263+OP 6*SI3+0E NO QVIV I*003+OP I*S83+09 2*263+09 HN-G9 NO GVIV I'993+00 E*I23-OI NO GVIV I'9L3+00 I*EI3+OP I'ZE3+09 33-SS t*Lt3+0t E'S23+07 L*LL3+0E NO QVIV NO GY1V I*It3+OS E*BL3+OE 33-S6 2*OL3+OP E*Et3+0t I'9L3+OP NO GV1V NO GY1V I*EL3+09 L*OL3+0t 30-90 NO GY1V I'LL3+0E E*t93+0E NO GY1V NO QVIV I*II3+09 E*>t3+0t 30-90 NO QVIV I'EI3+0) 2*E93+0D NO QVIV NO QVIV L*OL3+09 6*9E3+0P NI-9E 8'ZI3+OS t*9E3+0t E'803+09 NO GY1V NO QVIV 3*LE3+OS 9*EE3+0E NI-9S 2*663+00 2*693-01 I*9D3-OT NO GY1V NO QVIV 8*I83+0E 8*t03+0> 3n-9P NO QVIV I*663+00 I*OL3+00 NO QVIV 9*0E3+00 6*983+0E E'9L3+09 2N-9S )*E93+OP I*IE3+OS L*0E3+OP NO QVIV L*It3+0t 6*653+OS I'9E3+07 2N-96 9*L03-02 6*993-02 8*623-OE NO QVIV S'893-OE I*tE3+0E I*023+0t ! 8H-8E NO QVIV NO QVIV t*Lt3+02 NO QVIV NO QVIV NO QVIV I'IE
- L03-IS, .
I HH-8P NO QVIV NO 2EIV 9*t83+02 NO GVIV NO QVIV NO QVIV I'IE
- L03-IS 98-8S NO QVIV NO ])1V Z*SE3+OI NO GY1V NO GY1V NO QVIV I'IE ' L 03-IS I
HE-89 NO QVIV I'iG3+OS I*IP3+OS NO GY1V NO QVIV NO QVIV L*663+0E HU-88 NO GY1V S'9Z3+0E E'993+02 NO GY1V NO QVIV NO QVIV I*LE3+OI l 88-86 NO GVIV E't93+02 E'863+02 NO QVIV NO QVIV NO QVIV I*063+00 SH-06 S*663+09 NO QVIV I'L23+09 NO GY1V NO QVIV 3*I93+09 I'9L3+OS 1H-60 I*OI3+08 NO QVIV 9*tt3+09 NO GY1V NO QVIV I*t83+OL E*tE3+OS SM-6I I'ZI3+02 NO QVIV t'963+00 NO GVIV NO QVIV S*EE3+ot l I*Lt3+OS 1 SH-62 I*E13+OI NO QVIV S*ES3-OI NO QVIV NO QVIV E*t03+09 3*tE3+09 { A-60 t*II3+0E NO GY1V I*II3+02 NO QVIV NO QV.TL Z 933+0S E'993+OS i A-6Im g*OL3-01 NO QVIV I*8p3-02 NO QVIV NO QVIV 2*8I3+0E T*L23+0E A-61 6*It3+09 NO QVIV E*P)3+0P NO QVIV NO QVIV E*9E3+09 I*8t3+OS A-62 Z*OP3+OI NO GY1V S'8I3-OI NO QVIV NO QV1f' E*E63+OP E*Ed3+OS A-6E I*893+0Z NO GVIV S*II3+00 NO GY1V NO QVIV L*))3+0P E*863+OS 2H-6S I*603+OS t*I83+0P E*L03+0t NO GVIV S*693+0P 9*113+0t ZH-6L 2*EE3+09, I*883+0E Z*L33+01 I*903+01 NO QVIV E*863+01 I*IE3+OS E*SI3+OS NG-6S 2*ES3+0t 6*I83+0E 9*SS3+0E NO QVIV 0*9Z3+0E 9*It3+OS E'L03+0t HO-66 NO QVIV I*LE3+OE )*E93+01 NO QVIV E*623+0E I*ES3+OS I*Et3+09 13-66m I*L83-0E E*t03-OE S*LL3-02 NO GYIV S*043-02 6*SI3+02 )*8I3+0E 13-101 8*I03-0S 8*SI3-0S I*003-0E NO QVIV I*>93-OC 9*8)3+02 I*9E3+OI un-10E 2*L63+0E NO GVIV I*OL3+0E NO QVIV L*0E3+0E 9*923+09 P*t83+0) un-IOS I*SE3+00 NO QVIV S*SS3-OI NO GY1V I*Et2+00 I*S63+09 6*6S3+ot Bn-I09 I*E93+OS NO QVIV I'963+09 NO GVIV I'9t3+OS I*tE3+OL t*363+0S YO-IIOW I'963+0t I*It3+09 6'It3+0E NO GY1V E*IE3+09 S*t03+09 I*003+OS 13-Igsm 9*LE3+OE Z*EE2+OE 6'It3+OZ I*623+0E NO GY1V )*LL3+OS E*E83+OP 13-IZLm g*)63+09 8*SS3+0E E*023+0E 9*OL3+0E 9*E93+09 I*t83+09 L*It3+0t 13-TEL E'LL3+00 6*9I3-01 9*II3-OI I*693+00 L*OL3+00 I*003+0t s'9Z3+ot 13-126m I*633+0t 9*8S3+OE E*0t3+0E 9*EE3+0E S*0E3+OP I*t93+09 I'8E3+OS 13-IZ6 ! 6*LL3-02 E*S03-02 2*E03-02 L*It3-OZ Z*St3-OI 2*6E3+0E E*SS3+09 13-IEIm I*Et3+OE S*6Z3+01 S'OL3+OI 6*LL3+OI t*003+02 Z*093+0S E*083+OS 13-IEI Z'It3-OE 8'PP3-OE 9*563-OE I*L03-02 S*883-02 2*053+0E I*EE3+0E ! l 31 INION-I E-98 BM*I9-L/6L
CPS-ODCM TABLE 3.5-14 (continued) INHALATION PATHWAY FACTORS - R'm (CHILD) (mrem /yr per pCi/m') ORGAN: BONE LIVER T. BODY THYROID FIDNEY . LUNG GI-LLI ISOTOPE TE-132 4.81E+02 2.72E+02 2.63E+02 3.17E+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 I-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 3.20E+03 I-133 1.66E+04 2.03E+04 7.70E+03 3.85E+06 3.38E+04 NO DATA 5.48E+03 l I-134 1.17E+03 2.16E+03 9.95E+02 5.07E+04 3.30E+03 NO DATA 9.54E+02 I-135 4.92E+03 8.73E+03 4.14E+03 7.92E+05 1.34E+04 NO DATA 4.44E+03 - CS-134 6.51E+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 1.16E+05 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 BA-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 6.48E401 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 2.25E+02 7.55E+01 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 3.66E+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 DATA 1.17E+06 1.20E+07 3.89E+05 '- PR-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 V-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' ** Loss than 3.70 x 10*
l l l A CLINTON-1 3-69 Rev.15-7/97
CPS-ODCM TABLE 3.5-15 INHALATION PATHWAY FACTORS - R'm (TEEN) l (mrem /yr per pCi/m ) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE H-3 NO DATA 1.27E+03* 1.27E+03 1.27E+03 1.27E+03 1.27E+03 1.27E+03 C-14 2.60E+04 4.87E+03 4.87E+03 4.87E+03 4.87E+03 NA-24 4.87E+03 4.87E+03 1.38E+04 1.38E+04 1.38E+04 1.38E+04 1.38E+04 1.38E+04 1.38E+04 P-32 1.89E+06 1.10E+05 7.16E+04 NO DATA NO DATA NO DATA CR-51 NO DATA 9.28E+04 NO DATA 1.35E+02 7.50E+01 3.07E+01 2.10E+04 MN-54 NO DATA 5.11E+04 3.00E+03 8.40E+03 NO DATA 1.27E+04 1.90E+06 6.68E+04 MN-56 NO DATA 1.70E+00 2.52E-01 NO DATA 1.79E+00 FE-55 1.52E+04 5.74E+04 l 3.34E+04 2.38E+04 5.54E+03 NO DATA NO DATA 1.24E+05 FE-59 1.59E+04 3.70E+04 6.39E+03 1.43E+04 NO DATA NO DATA 1.53E+06 1.78E+05 CO-58 NO DATA 2.07E+03 2.78E+03 NO DATA NO DATA CO-60 1.34E+06 9.52E+04 NO DATA 1.51E+04 1.98E+04 NO DATA NO DATA 8.72E+06 NI-63 5.80E+05 4.34E+04 2.59E+05 1.98E+04 NO DATA NO DATA 3.07E+05 1.42E+04 HI-65 2.18E+00 2.93E-01 1.27E-01 NO DATA NO DATA 9.36E+03 CU-64 NO DATA 2.03E+00 3.67E+04 8.48E-01 NO DATA 6.41E+00 1.11E+04 6.14E+04 ZN-65 3.86E+04 1.34E+05 6.24E+04 NO DATA 8.64E+04 1.24E+06 4.66E+04 ZN-69 4.83E-02 9.20E-02 6.46E-03 NO DATA 6.02E-02 CR-83 1.b8E+03 2.85E+02 NO DATA NO DATA 3.44E+02 NO DATA NO DATA BR-84 NO DATA NO DATA NO DATA LT8E-15** 4.33E+02 NO DATA NO DATA NO DATA LT8E-l'5 BR-85 NO DATA NO DATA 1.83E+01 NO DATA NO DATA NO DATA LT8E-15 RB-86 NO DATA 1.90E+05 8.40E+04 NO DATA NO DATA RB-88 NO DATA 1.77E+04 NO DATA 5.46E+02 2.72E+02 NO DATA NO DATA NO DATA 2.92E-05 RB-89 NO DATA 3.52E+02 2.33E+02 NO DATA NO DATA SR-89 4.34E+05 NO DATA 3.38E-07 NO DATA '1.25E+C4 NO DATA NO DATA 2.42E+06 3.71E+05 JR-90 1.08E+08 NO DATA 6.68E+06 NO DATA NO DATA 1.65E+07 SR-91 7.65E+05 8.80E+01 NO DATA 3.51E+00 NO DATA NO DATA 6.07E+04 2.59E+05 SR-92 9.52E+00 NO DATA 4.06E-01 NO DATA NO DATA Y-90 2.74E+04 1.19E+05 2.98E+03 NO DATA 8.00Ef01 NO DATA NO DATA 2.93E+05 5.59E+05 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 ER-95 1.46E+05 4.58E+04 3.15E+04 NO DATA 6.74E+04 ER-97 1.38E+02 2.72E+01 2.69E+06, 1.49E+05 1.26E+01 NO DATA 4.12E+01 1.30E+05 6.30E+05 NW-95 1.86E+04 1.03E+04 5.66E+03 MO DATA MO-99 1.00E+04 7.51E+05 9.68E+04 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 RU-103 6.67E+02 8.72E-07 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 AG-110m 1.61E+07 9.60E+05 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 1.4U.+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 TE-127 1.66E+06 1.59E+05 2.01E+00 9.12E-01 4.42E-01 1.42E+00 7.28E+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 TE-131m 3.30E+03 1.62E+03 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 l 2.34E+03 1.51E+01 l CLINTON-1 3-70 Rev.15-7/97{J
CPS-ODCM TABLE 3.5-15 (continued) INHALATION PATHWAY FACTORS - R'm (TEEN) (mrem /yr per pCi/m') ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE TE-132 3.60E+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 1.51E+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 8.88E+02 2.32E+03 8.40E+02 3.95E+04 3.66E+03 NO DATA 2.04E+01 I-135 3.70E+03 9.445+03 3.49E+03 6.21E+05 1.49E+04 NO DATA 6.95E+03 CS-134 5.02E+05 1.12E+06 5.49E+05 NO DATA 3.75E+05 1.46E+05 9.76E+03 CS-136 5.15E+04 1.94E+05 1.37E+05 NO DATA 1.10E+05 1.78E+04 1.09E+04 CS-137 6.70E+05 8.48E+05 3.11E+05 NO DATA 3.04E+05 1.21E+05 8.48E+03 CS-138 4.66E+02 8.56E+02 4.46E+02 NO DATA 6.62E+02 7.87E+01 2.70E-01 BA-139 1.34E+00 9.44E-04 3.90E-02 NO DATA 8.88E-04 6.46E+03 6.45E+03 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-142 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 LA-142 9.60E-01 4.2SE-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 CE-143 2.66E+02 1.94E+02 2.16E+01 NO DATA 8.64E+01 1.30E+05 2.55E+05 CE-144 4.89E+06 2.02E+06 2.62E+05 NO DATA 1.21E+06 1.34E+07 8.64E+05 PR-143 1.34E+04 5.31E+03 6.62E+02 NO DATA 3.09E+03 4.83E+05 2.14E+05 PR-144 4.30E-02 1.76E-02 2.18E-03 NO DATA 1.01E-02 1.75E+03 2.35E-04 RD-147 7.86E+03 8.56E+03 5.13E+02 NO DATA 5.02E+03 3.72E+05 1.82E+05 1-187 1.20E+01 9.76E+00 3.43E+00 NO DATA NO DATA 4.74E+04 1.77E+05 dP-239 3.38E+02 3.19E+01 1.77E+01 NO DATA 1.00E+02 6.49E+04 1.32E+05
*1.27 x 10' **L ss than 8.00 x 10
- l LINTON-1 3-71 Rev.15-7/97
3dS-OGDH 1VHI'3 E
- S-I 9 I
INHV7V1 ION dVIHMVA dVD1OUS - 8 % )V0071(
)maam/X2 da2 tr o T / m (
OHDVN' GON3 I'I A3H 1 GOGA 1HAUOIG XIGN3A I'nND IS01Od3 DI-ITI H-E NO GVIV I*293&0E, I*E93t0E I*293+0E I*293+0E I*293+0E 3-ID I*823+OP I*293+0E E'tI3+0E C*PI3+0E C*tI3+0E E*tI3+0E C*tI3+0E E*tI3+0E NV-2P I*023+ot I*023+JP I*023+0D I'023+0# I*023+0# I*023+OP d-EZ I*023+OP I*E23+09 L*lI3+OP S'OI3+OP NO QVIV NO GVIV NO QVIV 3H-SI NO OVIV 8*9k3+0k NO GV1V I*003+02 S*6S3+OI 2'283+01 I'tt3+OP E*E23+0E HN-SP NO QVIV E*693+OP 9*E03+0E NO OVIV 6*8>3+0E I*t03+09 L*Lt3+0> HN-S9 NO QVIV I*ZD3+00 I*8C3-OI NO OVIV I*E03+00 6*P)3+00 Z*023+0> 33-SS- Z*t93+OP I'L03+0t E*6P3+0E NO GY1V NO GY1V L*EI3+09 9"0E3+0E 33-S6 I*I83+OP 2*L83+OP I*093+OP NO GY1V NO GY1V I*023+09 I'883+OS 30-90 NO GVIV I*S03+0E E*OL3+0E NO OVIV NO GY1V 6*283+OS I*093+OS 30-90 NO GY1V I*IS3+OP I*t83+09 NO GY1V NO GY1V S*6L3+09 2*893+0S NI-9E )*E23+OS E*IP3+OP I*PG3+OP NO QVIV NO GY1V I'L83+OS NI-9S I*St3+00 I*Et3+09 Z*T03-OI 6'I33-02 MO OVIV NO GY1V S'903+0E I*2E3+OP 3n-99 NO GY1V I*>93+00 9'193-01 NO QVIV t*923+00 9'L83+0E P*603+0t 3M-95 E*Et3+0t I'0E3+OS t'993+09 NO QVIV 9*603+07 8*9t3+OS S*Et3+0t 2N-96 E*E83-OZ 9'SI3-02 t*SE3-OE NO GV1Y t*323-02 6'203+02 GH-8E NO QVIV I*9E3+OI NO QVIV E*tI3+02 NO GY1V NO QVIV NO GYIV Z*EE3+OZ dE-89 NO UY1V NO QVIV E*IE3+02 NO QVIV NO QVIV NO QVIV I'993-0E HH-89 NO GY1V NO QVIV I*283+0I NO QVIV NO QVIV NO QVIV I'18 3-IS, . 38-89 NO QVIV I*ES3+OS 9*603+0P NO GYIV NO QVIV NO GY1V I*993+0t HH-88 NO QVIV E*8L3+02 I*6E3+OZ NO QVIV NO QVIV NO QVIV E*EP3-06 UG-86 NO GVIV 2*S93+02 I*L03+02 NO GY1V NO GVIV NO QVIV 6*Z83-IZ SH-86 E*093+OS NO QVIV 8*LE3+0E NO QVIV NO QVIV I*)03+09 E*S03+OS ISH-60 6 633+04 NO QVIV 9*T03+09 NO GY1V NO GY1V 6'903+09 L*2E3+OS SH-6I 9*163+01 NO QVIV E*S03+00 NO GY1V NO QVIV SH-6E E*993+0t I*6I3+OS 9
- L t 3+00 NO QVIV E*6I3-OI NO QVIV NO QVIV I'993+09 t'E03+0#
A-60 Z*063+0E NO GVIV S*9I3+01 NO QVIV NO QVIV I*L03+OS S*093+0S A-6Im Z 9I3-0T NO QVIV I*023-02 NO QVIV NO GVIV I*623+0E I*EE3+00 A-6I t'933+OS NO QVIV I*Et3+0t NO QVIV NO GVIV I*L03+09 E'8S3+OS A-6E I*0E3+01 NO QVIV E*023-OI NO QVIV NO QVIV I*SL3+OP L*ES3+OP A-6E 6'>>3+01 NO GV1Y 2*9I3+00 NO QVIV NO QVIV t*893+ot t*223+09 2H-69 I*OL3+OS E*tP3+0t E*EE2+OP NO GY1V S*tZ3+ot 3H-6L I'LL3+09 I*S03+OS 6*983+01 I*693+01 6*0t3+00 NO QVIV 3*6L3+OI L*8L3+0t' S*ZE3+OS NE-6S I*tI3+07 L*823+0E )*EI3+0E NO GY1V L*Lt3+0E HO-66 G*093+OS I*093+OS NO QVIV I"EI3+0E Z*E03+OI NO GY1V Z*6I3+02 6'IE3+0t E*t83+09 13-66m I*0E3-0E Z*613-OE E*L03-02 NO QVIV t*t32-02 4*9t3+02 t*I93+0E
.f3-101 t*I83-0S 9*023-0S S'603-09 NO GY1V I*083-0E E*663+02 I*063-II un-I0E I*SE3+0E NO QVIV 9'S83+0E NO QVIV 9*8E3+0E 9*OS3+OS I*I03+OS un-IOS L*603-01 NO UY1V E'II3-01 NO GVIV I*023+00 I*T03+07 )"823+OP un-109 9*6I3+09 NO OVIV 8*L33+0E NO GVIV I*Et3+09 6*E93+09 6*I23+0S yc.Itom I*083+09 I*003+0D S*6t3+0E NO QVIV I*6L3+09 t*9E3+09 E*033+OS 13-125M E*tE3+0E I*S83+OE t'9L3+02 I*093+0E I'Z)3+09 E'It3+OS L*093+OP 13-IZLm I'293+09 S*LL3+OE I*SL3+0E E*263+0E )*983+09 6*903+OS I*S03+OS 12-IZL I*t03+00 9*)23-01 E*I03-OI I*093+00 S I03+00 13-IE6m 9*SI3+0E S*Lt3+OP 6*L93+0E t'9L3+0E I*S83+0E E*Pt3+0E E'993+OP 13-126 I*I93+09 E'8E3+09 t*683-02 E*E63-02 I*Et3-02 E*603-02 I*8L3-OI I*693+0E I*SL3+02 I3-IEIm 9*663+01 t*E93+OI Z*603+01 S*S03+OI E*063+0E 13-IEI I't93+OS S*S93+OS I*II3-02 S*6S3-OE E*S63-OE 6*E93-0E )*EL3-OZ I*E63+0E I*9t3+OI DI' INION-I E-LE d*LiLWL
CPS-ODCM TABLE 3.5-16 (continued) INilALATION PATHWAY FACTORS - R'.y (ADULT) (mrem /yr per pCi/m') i ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE TE-132 2.60E+02 2.15E+02 1.62E402 1.90E+02 1.46E+03 2.88E+05 5.10E+05 I-130 4.58E+03 1.34E+04 5.28E403 1.14E+06 2.09E+04 NO DATA 7.69E+03 I-131 2.52E+04 3.58E+04 2.05E+04 1.19E+07 6.13E+04 NO DATA 6.28E+03 I-132 1.16E+03 3.26E+03 1.16E+03 1.14E+05 5.18E+03 NO DATA 4.06E+02 I-133 8.64E+03 1.48E+04 4.52E+03 2.15E+06 2.58E+04 NO DATA 8.88E+03 I-134 6.44E+02 1.73E+03 6.15E+02 2.98E+04 2.75E+03 NO DATA 1.01E+00 1-135 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 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 LA-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 4.64E+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 7.05E-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 f-187 8.48E+00 7.08E+00 2.48E400 NO DATA NO DATA 2.90E+04 1.55E+05 tlP-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'
- Less than 8.00 x 10-"
i I
~ l l.
CT.T NTON- 1 3-73 Rev.15-7/97
1 CPS-ODCM TABLE 3.5-17 COW MILK PATHWAY ACTORS - R h (INFANT) f (m' rem /yr per pCi/sec) { ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE H-3 NO DATA 2.38E403* 2.38E+03* 2.38E+03* 2.38E+03* 2.38E+03* 2.38E+03* C-14 3.23E+06* 6.89E+05* 6.89E+05* 6.89E+05* 6.89E+05* 6.89E+05* NA-24 1.55E+07** 6.89E+05* 1.55E+07 1.55E+07 1.55E+07 1.55E+07 1.55E+07 1.55E+07 P-32 1.60E+11 9.41E+09 6.20E+09 NO DATA NO DATA NO DATA CR-51 NO DATA 2.16E+09 i NO DATA 1.61E+05 1.05E+05 2.29E+04 2.04E+05 4.69E+06 l MN-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 FE-55 2.84E+00 1.35E+08 8.72E+07 2.33E+07 NO DATA NO DATA 4.26E+07 1.11E+07 FE-59 2.2SE+08 3.92E+08 1.55E+08 NO DATA NO DATA 1.16E+08 CO-58 1.87E+08 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 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 0.52E+04 NO DATA 3.11E+05 ZN-65 NO DATA 3.78E+06 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 1.4SE-11 NO DATA 2.85E-09 liR-83 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA j PR-84 NO DATA i NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA RR-85 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA RB-86 NO DATA 2. 23E4'10 1.10E+10 NO DATA NO DATA 1 RB-88 NO DATA 5.70E+08 j NO DATA 1.88E-44 1.03E-44 NO DATA NO DATA No DATA 1.83E-44 I RB-89 NO DATA 3.43E-52 2.36E-52 NO DATA NO DATA NO DATA 1.17E-52 l S R-8 9 1.26E+10 NO DATA 3.61E+08 NO DATA NO DATA NO DATA 2.59E+08 l
}SR-90 1.22E+11 NO DATA 3.10E+10 NO DATA NO DATA NO DATA 1.52E+09
'SR-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 Y-91m 6.09E-19 NO DATA 2.00E-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 DAT 8.28E+05 ZR-97 4.03E+00 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 HO-99 NO DATA 2.07E+08 4.04E+07 NO DATA 3.10E+08 NO DATA 6.83E+07 TC-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 l 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 l l 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 ) l CLINTON-1 3-74 Rov.15 '7/47
I CPS-ODCM TABLE 3.5-17 (continued) COW MILK PATHWAY FACTORS - R au (INFANT) (m' mrem /yr per pCi/sec) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE 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 8.70E+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 _I-135 1.13E+05 2.24E+05 8.18E+04 2.01E+07 2.50E+05 NO DATA 8.12E+04 CS-134 3.65E+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 CS-137 5.15E+10 6.03E+10 4.27E+09 NO DATA 1.62E+10 6.44E+09 1.89E+08 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 i BA-142 2.32E-79 1.93E-82 1.14E-80 NO DATA 1.11E-82 1.17E-82 9.56E-79 IA-140 4.0$E+01 1.60E+01 4.11E+00 NO DATA NO DATA NO DATA 1.88E+05 IA-142 1.73E-10 6.34E-11 -1.52E-11 NO DATA NO DATA NO DATA 1.08E,05 ; CE-141 4.34E+04 2.65E+04 3.12E+03 NO DATA 8.17E+03 NO DATA 1.37E+07 CE-143 3.98E+02 2.64E+05 3.01E+01 NO DATA 7.69E+01 NO DATA 1.54E+06 ] CE-144 2.34E+06 9.56E+05 1.31E+05 NO DATA 3.87E+05 NO DATA 1.34E+08 PR-143 1.49E+03 5.56E+02 7.37E+01 NO DATA 2.07E+02 NO DATA 7.85E+05 PR-144 6.27E-53 2.43E-53 3.16E-54 NO DATA 8.79E-54 NO DATA 1.13E-48 ND-147 8.79E+02 9.03E+02 5.53E+01 NO DATA 3.48E+02 NO DATA 5.72E+05 J-187 6.10E+04 4.24E+04 1.46E+04 NO DATA NO DATA NO DATA 2.49E+06 f,;P-239 3.64E+01 3.26E+00 1.84E+00 NO DATA 6.49E+00 NO DATA 9.41E+04
- mrem /yr per Ci/m'
- 1.55 x 10' CLINTON-1 3-75 Rev.15-7/97
CPS-ODCM TABLE 3.5 9 l COW MILK PATHWAY FACTORS - R'm (CHILD) (m# mrem /yr per pCi/sec) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG ISOTOPE GI-LLI H-3 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+05* 3.29E+05* 3.29E+05* 3.29E+05* 3.29E+05* NA-24 3.29E+05* 8.93E+06** 8.93E+06 8.93E+06 8.93E+06 8.93E+06 8.93E+06 8.93E+06 P-32 7.79E+10 3.64E+09 3.00E+09 NO DATA NO DATA NO DATA CR-51 NO DATA 2.15E+09 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 1.20E-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 FE-59 1.20E+08 1.10E+07 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 NI-65 1.65E+00 1.56E-01 9.10E-02 NO DATA NO DATA NO DATA CU-64 NO DATA 1.91E+01 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 DATA 6.92E+09 NO DATA ZN-69 1.93E+09 9.11E-12 1.32E-11 1.22E-12 NO DATA 7.99E-12 CR-83 NO DATA NO DATA 8.30E-10 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA ER-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 RB-88 NO DATA 5.65E+08 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 SR-89 6.63E+09 NO DATA 1.22E-54 NO DATA 1.89E+08 NO DATA NO DATA NO DATA 2.57E+08 R-90 1.12E+11 NO DATA 2.84E+10 NO DATA NO DATA NO DATA 1.51E+09 4R-91 1.30E+05 NO DATA 4.89E+03 NO DATA NO DATA NO DATA 2.86E+05 SR-92 2.20E+00 NO DATA 8.83E-02 NO DATA NO DATA Y-90 3.23E+02 NO DATA 4.17E+01 NO DATA 8.65E+00 NO DATA NO DATA NO DATA 9.20E+05 i 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 1.04E+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 ER-97 NO DATA 8.80E+05 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 MO-99 NO DATA 2.29E+08 NO DATA 8.15E+07 2.02E+07 NO DATA 1.74E+08 NO DATA 6.74E+07 TC-99m 1.32E+01 2.5BE+01 4.28E+02 NO DATA 3.75E+02 TC-101 1.31E401 1.47E+04 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 RU-105 3.80E-03 NO DATA 1.11E+05 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 l AG-110m 2.09E+08 1.41E+08 1.13E+08 NO DATA 2.63E+08 TE-125m 7.39E+07 NO DATA 1.68E+10 2.00E+07 9.85E+07 2.07E+07 NO DATA NO DATA 7.13E+07 TE-127m 2.08E+08 5.61E+07 2.47E+07 4.98E+07 5.94E+08 TE-127 2.97E+03 NO DATA 1.69E+08 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 TE-129 NO' DATA 3.31E+08 1.28E-09 3.57E-10 3.04E-10 9.12E-10 3.74E-09 TE-131m 1.60E+06 NO DATA 7.96E-08 5.53E+05 5.88E+05 1.14E+06 5.35E+06 NO DATA 2.24E+07 TE-131 1.64E-32 5.01E-33 4.89E-33 1.26E-32 4.97E-32 NO DATA 8.63E-32 i CLINTON-1 3-76 Rev.15-7/97
i 4 CPS-ODCM TABLE 3.5-18 (continued) COW MILK PATHWAY FACTORS - Rh (CHILD) (m# mrem /yr per pCi/sec) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE i TE-132 1.03E+07 4.56E+06 5.51E+06 6.64E+06 4.23E+07 NO DATA 4.59E+07 I-130 1.72E+06 3.47E+06 1.79E+06 3.82E+08 5.19E+06 NO DATA 1.62E+06 I-131 1.30E+09 1.31E+09 7.44E+08 4.33E+11 2.15E+09 NO DATA 1.17E+08 I-132 6.91E-01 1.27E+00 5.84E-01 5.89E+01 1.94E+00 NO DATA 1.49E+00 1-133 1.72E+07 2.12E+07 8.03E+06 3.94E+09 3.54E+07 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 I-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 hO 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-81 LA-140 1.94E+01 6.78E+00 2.11E+00 NO DATA NO DATA NO DATA 1.89E+05 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 1.36E+07 j 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 PR-144 2.94E-53 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 NO DATA 5.69E+05 J-187 2.88E+04 1.71E+04 7.66E+03 NO DATA NO DATA NO DATA 2.40E+06 NP-239 1.72E+01 1.24E+00 8.69E-01 NO DATA 3.58E+00 NO DATA 9.15E+04
*mrtm/yr per pCi/m **8.93 x 10' 4
i I 1
- CLINTON-1 3-77 Rev.15-7/97 .
3dS-00DH 1VHI'3 E'S-16 DOM HIIW dVIHMVX 7 IWDIOHS - 8% )133N(
)W WJOW/dl dal lTD T (
OUDVN* GON3 I'I A3H 1*8OGA 1HAHOIG MIGN3A I'GND IS01Od3 DI-ITI H-C NO QVIV 6'623+02 6'623+02, 6*623+02 6*623+02, 6*623+02, 3-IP 9*L03+OS. I*Ep3+OS, 6*623+02+ I*Et3+OS. I*Ep3+OS, I*ED3+09, I'Et3+OS, I*Et3+OS, NV-EP >*263+09, t*Z63+09 t*263+09 >*263+09 )*263+09 )*263+09 d-EZ >*263+09 E*IS3+IO I*6S3+06 I*223+06 NO QVIV NO GVIV NO QVIV 2*9t3+06 38-5I NO QVIV NO GVIV S*003+06 2*L83+06 HN-SP NO QVIV I*T03&0t L'It3+0k 8*kI3+09 I't03+OL 2*L83+09 NO GY1V >*I63+09 NO GY1V 2*883+OL HN-S9 NO QVIV L*E23-OE I*E03-OC NO QVIV 6*393-0E NO QVIV 33-SS t*023-OI
)'t93+OL E'I93+OL L*E83+09 NO GVIV' NO GY1V 2*OI3+OL I*EL3+OL 33-96 S I83+OL I'ZI3+08 t'9L3+OL NO GVIV NO QVIV E'8I3+OL 30-98 2*983+08 NO QVIV L*683+09 I*8&3+OL NO QVIV NO GVIV NO QVIV I*103+00 30-90 NO QVIV 2*L83+OL 9*293+0L NO QVIV ffO QVIV NO QVIV NI-9E C*923+08 I*I83+IO 8*Et3+08 t'003+08 NO QVIV NO GV1Y NO QVIV I*EE3+08 N?-9S 9*t63-OI 8'9L3-02 E*693-02 NO QVIV NO QVIV NO QVIV 3n-99 )*L03+00 NO QVIV t'Z03+0t I*6L3+OP NO GVIV I*093+09 NO QVIV E*393+09 2N-9S 3*II3+06 L*EZ3+06 E'tI3+06 NO QVIV t'983+06 NO QVIV E*T03+06 2N-96 E*L03-IZ L*093-12 t*6)2-IE NO QVIV t*9I3-IZ NO GVIV GM-8E I*E03-II NO QVIV NO QVIV NO QVIV NO QVIV NO QVIV NO QVIV EH-GP NO QVIV NO GV1Y- NO QVIV NO QVIV NO QVIV NO GY1V NO QVIV NO GYIV GH-8S NO QVIV NO GVIV NO QVIV NO QVIV NO QVIV NO GY1V NO GY1V HG-89 NO GVIV t*Lt3+06 E*ZE3+06 NO QVIV NO QVIV NO GVIV HG-88 L*013+08 NO QVIV C*603-99 Z*083-PS NO QVIV NO QVIV NO QVIV H9-06 E*Et3-SZ NO QVIV L*683-SE S*9P3-SE NO QVIV NO QVIV NO OVIV I'223-91 kU-86 Z*983+06 NO QVIV L*9L3+OL NO QVIV NO QVIV NO GY1V E*I63+08 4-60 9*933+IO NO QVIV I'993+IO NO QVIV NO QVIV NO QVIV I'893+06 FH-6I S*ZL3+0P NO QVIV Z*I03+0E NO QVIV NO QVIV NO QVIV 2*E63+09 SU-6E 6'0E3-01 NO GVIV E"893-OZ NO QVIV NO GY1V NO QVIV E*E03+OI X-60 I*EI3+OZ NO QVIV E*SE3+00 NO QVIV NO QVIV NO GY1V I*083+09 X-6IW I*I83-I6 NO GY1V )'t63-ZI NO QVIV NO QVIV NO QVIV A-61 S*SS3-IO I*983+09 NO QVIV t*2)3+02 NO QVIV NO QVIV NO GY1V 9*t83+09 A-6E I*0E3-OP NO QVIV 2*6L3-09 NO QVIV NO QVIV NO QVIV Z*8Z3+00 X-6E t*T03-01 NO QVIV I*I23-02 NO QVIV NO QVIV NO QVIV I*393+0t 2H-69 I'953+0E S'Z03+02 E*S03+02 NO QVIV L*9S3+0E NO GY1V I*203+09 2H-6L L*8L3-OI I*593-OI L*IL3-OZ NO QVIV E*E93-OI NO GY1Y ,t*223+OP Nf69 I*tI3+OS L*8I3+OP >*E03+09 NO QVIV L*SL3+09 NO QVIV E*Et3+08 HO-66 NO QVIV t*t93+OL 8*S03+09 NO QVIV I*0Z3+08 13-66M NO QVIV L*683+04 S*LP3+00 I'903+OI Z*083+02 NO QVIV Z*E63+03 8*863+00 I*0S3+09 10-I01 S*223-90 L*tZ3-90 L*Z63-96 NO GY1V I*Et3-98 t*SZ3-90 I'ZL3-99 un-10E I*8I3+0E NO QVIV L*LE3+OZ NO QVIV 9*EL3+0E NO QVIV I*SI3+OS un-IOS I'993-OE NO QVIY 9*093-09 NO QVIV I*643-OZ NO QVIV I*E93+00 un-109 E'LS3+OP NO QVIV )*LE3+0E NO GYIV L*2E3+09 NO GY1V VD-IIOM I'803+09 6*9t3+OL 6'I33+04 S*SS3+OL NO QVIV I'Lt3+00 NO QVIV Z*993+IO 13-Iggm E*OI3+OL I*083+OL t*023+09 8*tI3+09 NO QVIV NO GY1V 8*883+OL 13-IgLm 8*tE3+OL Z*663+OL I*003+OL 2*OI3+OL E*)23+08 NO GVIV Z*I03+00 13-IEL I*Z13+0E t*303+02 E*903+03 8*EE3+02 t*863+0E NO QVIV 6*EE3+09 13-IE6W I*T03+08 t*063+04 I*Lt3+OL E'993+OL t'9I3+08 NO GV1Y t*It3+08 13-IE6 S*183-IO I*6E3-IO I*293-IO E'L03-IO 2*It3-06 NO QVIV Z*8E3-06 I 13-IEIW 9*993+OS E*IS3+OS Z*9E3+09 t'LE3+OS E'Z83+09 NO QVIV E*SE3+OL
) 13-IEI 9*L03-EE E'L93-EE Z*063-EE S*I93-EC E*623-EZ NO QVIV S*S03-EP DI' INION-I E-L8 "" L %L/oL
CPS-ODCM TABLE 3.5-19 (continued) COW MILK PATHWAY FACTORS - R".y (TEEN) (m* mrem /yr per pCi/sec) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE 1 TE-132 4.29E+06 2.72E+06 2.56E+06 2.87E+06 2.61E+07 NO DATA 8.61E+07 I-130 7.33E+05 2.12E+06 8.47E+05 1.73E+08 3.27E+06 NO DATA 1.63E+06 { I-131 5.36E+0B 7.50E+08 4.03E+08 2.19E+11 1.29E+09 -NO DATA 1.48E+08 I-132 2.90E-01 7.59E-01 2.72E-01 2.56E+01 1.20E+00 NO DATA 3.31E-01 I-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 I-135 2.29E+04 5.90E+04 2.19E+04 3.80E+06 9.32E+04 NO DATA 6.54E+04 CS-134 9.79E+09 2.30E+10 1.07E+10 NO DATA 7.32E+09 2.80E+09 2.87E+08 CS-136 4.48E+08 1.76E+09 1.18E+09 NO DATA 9.59E+08 1.51E+08 1.42E+0B CS-137 1.33E+10 1.77E+10 6.18E+09 NO DATA 6.03E+09 2.34E+09 2.52E+08 CS-138 1.58E-23 3.03E-23 1.51E-23 NO DATA 2.23E-23 2.60E-24 1.37E-26 -BA-139 8.20E-08 5.77E-11 2.39E-09 NO DATA 5.44E-11 3.98E-11 7.31E-07 BA-140 4.85E+07 5.95E+04 3.13E+06 NO DATA 2.02E+04 4.00E+04 7.49E+07 BA-141 7.98E-46 5.96E-49 2.67E-47 NO DATA 5.53E-49 4.08E-49 1.70E-51 BA-142 4.54E-80 4.54E-83 2.80E-81 NO DATA 3.85E-83 3.02E-83 1.40E-9.1 IA-140 8.11E+00 3.98E+00 1.06E+00 NO DATA NO DATA NO DATA 2.29E+05 IA-142 3.42E-11 1.52E-11 3.78E-12 NO DATA NO DATA NO DATA 4.62E-07 'CE-141 8.88E+03 5.93E+03 6.81E+02 NO DATA 2.79E+03 NO DATA 1.70E+07 CE-143 7.64E+01 5.55E+04 6.21E+00 NO DATA 2.49E+01 NO DATA 1.67E+06 CE-144 6.61E+05 2.73E+05 3.55E+04 NO DATA 1.63E+05 NO DATA 1.66E+08 PR-143 2.91E+02 1.16E+02 1.45E+01 NO DATA 6.75E+01 NO DATA 9.57E+05 PR-144 1.19E-53 4.88E-54 6.04E-55 NO DATA 2.80E-54 NO DATA 1.31E-56 ND-147 1.81E+02 1.97E+02 1.18E+01 NO DATA 1.16E+02 NO DATA 7.10E+05 l-187 1.19E+04 9.72E+03 3.41E'+03 NO DATA NO DATA NO DATA 2.63E+06 NP-239 6.99E+00 6.59E-01 3.66E-01 NO DATA 2.07E+00 NO DATA 1.06E+05
*mrsm/yr per pCi/m **4.29 x 10' I
i d l i l CT.TNTON-1 3-79 Rev.15-7/97
CPS-ODCM TABLE 3.5-20 COW MILK PATHWAY FACTORS - RS 3 (ADULT) l (m* mrem /yr per pCi/sec) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE H-3 NO DATA 7.62E+02* 7.62E+02* 7.62E+02* 7.62E+02* 7.62E+02* C-14 3.63E+05* 7.26E+04* 7.62E+02* 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+08 NO DATA NO DATA CR-51 NO DATA 1.92E+09
~
NO DATA NO DATA 2.85E+04 1.70E+04 6.27E+03 MN-54 3.78E+04 7.16E+06 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 FE-59 9.68E+06 9.95E+06 2.97E+07 6.99E+07 2.68E+07 NO DATA NO DATA 1.95E+07 CO-58 2.33E+08 NO DATA .4.72E+06 1.06E+07 NO DATA NO DATA NO DATA CO-60 NO DATA 1.64E+07 9.57E+07 3.62E+07 NO DATA NO DATA NO DATA 3.08E+08 NI-63 6.73E+09 4.67E+08 2.26E+08 NO DATA NO DATA NO DATA NI-65 3.70E-01 9.74E+07 4.81E-02 2.19E-02 NO DATA NO DATA NO DATA CU-64 No DATA 2.36E+04 1.22E+00 1.11E+04 NO DATA 5.94E+04 NO DATA 2.01E+06 EN-65 1.37E+09 '4.37E+09 1.98E+09 NO DATA 2.93E+09 NO DATA 2.75E+09 EM-t 9 2.01E-12 3.84E-12 2.67E-13 BR-83 NO DATA 2.50E-12 NO DATA 5.77E-13 NO DATA NO DATA NO DATA NO DATA NO DATA _ER-84 NO DATA NO DATA NO DATA NO DATA NO DATA No DATA NO DATA NO DATA BR-85 NO DATA NO DATA l NO DATA NO DATA NO DATA NO DATA NO DATA RB-86 NO DATA NO DATA 2.60E+09 1.21E+09- NO DATA NO DATA No DATA RB-88 NO DATA 2.15E-45 5.12E+08 1.14E-45 NO DATA NO DATA NO DATA 2.97E-56 RB-89 NO DATA 4.49E-53 3.16E-53 NO DATA SR-89 NO DATA NO DATA 2.61E-66 1.45E+09 NO DATA 4.16E+07 NO DATA NO DATA K-90 4.68E+10 NO DATA 2.33E+08 NO DATA 1.15E+10 NO DATA NO DATA No DATA dR-91 2.87E+04 1.35E+09 NO DATA 1.16E+03 NO DATA NO DATA NO DATA SR-92 4.92E-01 1.37E+05 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 Y-91m 6.42E-20 NO DATA 2.49E-21 NO DATA Y-91 NO DATA NO DATA 1.89E-19 8.60E+03 'NO DATA 2.30E+02 NO DATA NO DATA Y-92 5.57E-05 NO DATA 4.73E+06 NO DATA 1.63E-06 NO DATA NO DATA NO DATA 9.75E-01 Y-93 2.22E-01 NO DATA 6.12E-03 NO DATA ER-95 NO DATA NO DATA 7.03E+03 9.45E+02 3.03E+02 2.05E+02 NO DATA 4.76E+02 ER-97 4.32E-01 NO DATA 9.61E+05 8.71E-02 3.98E-02 NO DATA 1.32E-01 NO DATA ' 2.70E+04 NB-95 8.25E+04 4.59E+04 2.47E+04 No DATA 4.54E+04 NO DATA 2.79E+08 MO-99 NO DATA 2.48E+07 4.72E+06 TC-99m NO DATA 5.61E+07 NO DATA 5.74E+07 3.31E+00 9.35E+00 1.19E+02 NO DATA 1.42E+02 TC-101 2.85E-60 4.58E+00 5.53E+03 4.11E-60 4.03E-59 NO DATA 7.41E-59 2.10E-60 1.24E-71 RU-103 1.02E+03 NO DATA 4.39E+02 NO DATA 3.89E+03 NO DATA 1.19E+05 RU-105 8.52E-04 NO DATA 3.36E-04 RU-106 NO DATA 1.10E-02 NO DATA 5.21E-01 2.04E+04 NO DATA 2.58E+03 NO DATA 3.94E+04 AG-110m 5.82E+07 NO DATA 1.32E+06 5.39E+07 3.20E+07 No DATA 1.06E+08 NO DATA TE-125m 1.63E+07- 5.91E+06 2.20E+10 2.19E+06 4.91E+06 6.64E+07 NO DATA 6.52E+07 TE-127m 4.58E+07 1.64E+07 5.58E+06 1.17E+07 TE-127 6.52E+02 1.86E+08 NO DATA 1.53E+08 2.34E+02 1.41E+02 4.83E+02 2.65E+03 TE-129m 6.01E+07 2.24E+07 NO DATA 5.14E+04 9.52E+06 2.07E+07 2.51E+08 NO' DATA 3.03E+08 TE-129 2.82E-10 1.06E-10 6.86E-11 TE-131m 2.16E-10 1.18E-09 NO DATA 2.12E-10 3.60E+05 1.76E+05 1.47E+05 2.79E+05 1.78E+06 _TE-131 3.68E-33 NO DATA 1.75E+07 1.54E-33 1.16E-33 3.03E-33 1.61E-32 NO DATA 5.22E-34 l CLINTON-1 3-80 nov.1s-7/o7]
CPS-ODCM TABLE 3.5-20 (continued) COW MILK PATHWAY FACTORS - Rh (ADULT) (m" mrem /yr per pCi/sec) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE TE-132 2.41E+06 1.56E+06 1.46E+06 1.72E+06 1.50E+07 NO DATA 7.36E+07 I-130 4.16E+05 1.23E+06 4.04E+05 1.04E+08 1.91E+06 NO DATA 1.06E+06 I-131 2.97E+08 4.24E+08 2.43E+08 1.39E+11 7.27E+08 NO DATA 1.12E+08 I-132 1.65E-01 4.40E-01 1.54E-01 1.54E+01 7.02E-01 NO DATA 8.27E-02
,I-133 3.86E+06 6.72E+06 2.05E+06 9.87E+08 1.17E+07 NO DATA 6.04E+06 I-134 1.89E-12 5.13E-12 1.83E-12 8.88E-11 8.15E-12 NO DATA 4.47E-15 I-135 1.29E+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 BA-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-55 BA-142 2.51E-80 2.58E-83 1.58E-81 NO DATA 2.18E-83 1.46E-83 3.54E-98 IA-140 4.53E+00 2.28E+00 6.03E-01 NO DATA NO DATA 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 1.2SE+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 '187 6.50E+03 5.43E+03 1.90E+03 NO DATA NO DATA NO DATA 1.78E+06
'NP-239 3.67E+00 3.60E-01 1.99E-01 NO DATA 1.12E+00 NO DATA 7.39E+04
*mrcm/yr per pCi/m
**2.46 x 10'
+
I i CLINTON-1 3-81 Rev.15-7/97 ]
1 CPS-ODCM TABLE 3.5-21 GOAT MILK PATHWAY FACTORS - Rh (INFANT) { (m# rem /yr per pCi/sec) i ORGAN: DONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE H-3 NO DATA 4.86E+03* 4.86E+03* 4.86E+03* C-14 4.86E+03* 4.86E+03* 4.86E+03* 3.23E+06* 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 6.89E+05* 1.87E+06 1.87E+06 1.87E+06 1.87E+06 i i P-32 1.90E+11 1.12E+10 7.46E+09 NO DATA NO DATA NO DATA CR-51 NO DATA NO DATA 2.58E+09 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 i 3.22E-03 NO DATA 3.40E-01 FE-55 1.75E+06 1.13E+06 3.02E+05 NO DATA NO DATA FE-59 5.53E+05 1.44E+05 2.91E+06 5.08E+06 2.00E+06 NO DATA NO DATA 1.50E+06 CO-58 NO DATA 2.43E+06 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 NI-65 4.20E-01 1.29E+07 4.76E-02 2.16E-02 NO DATA NO DATA NO DATA CU-64 NO DATA 2.04E+04 3.62E+00 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 ZN-69 2.32E-12 4.18E-12 3.11E-13 ER-83 NO DATA 1.74E-12 NO DATA 3.41E-10 NO DATA NO DATA NO DATA NO DATA NO DATA CR-84 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA i
BR-85 NO DATA NO DATA l NO DATA NO DATA NO DATA NO DATA NO DATA RB-86 NO DATA NO DATA NO DATA 2.65E+09 1.31E+09 NO DATA NO DATA NO DATA RB-88 NO DATA 2.25E-45 6.79E+07 1.23E-45 NO DATA NO DATA NO DATA 2.19E-45 RB-89 NO DATA 4.09E-53 2.82E-53 NO DATA SR-89 NO DATA NO DATA . 39E-53 2.64E+10 NO DATA 7.56E+08 NO DATA NO DATA
.BR-90 2.55E+11 NO DATA NO DATA 5.42E+08 6.50E+10 NO DATA NO DATA NO DATA 3.19E+09
'SR-91 5.65E+05 NO DATA 2.05E+04 NO DATA SR-92 NO DATA NO DATA 6.69E+05 9.83E+00 NO DATA 3.65E-01 NO DATA NO DATA Y-90 NO DATA 1.06E+02 0.19E+01 NO DATA 2.19E+00 NO DATA NO DATA Y-91m 7.29E-20 NO DATA 1.13E+05
- NO DATA 2.48E-21 NO DATA NO DATA NO DATA 2.43E-16 j Y-91 8.78E+03 No DATA 2.34E+02 NO DATA Y-92 NO DATA NO DATA 6.29E+05 6.4OE-05 NO DATA 1.80E-06 NO DATA NO DATA Y-93 2.55E-01 NO DATA 1.22E+00 NO DATA 6.95E-03 NO DATA NO DATA NO DATA 2.02E+03 ZR-95 8.16E+02 1.99E+02 1.41E+02 ZR-97 NO DATA 2.14E+02 NO DATA- 9.90E+04 4.85E-01 8.33E-02 3.80E-02 NO DATA 8.40E-02 NB-95 7.12E+04 NO DATA 5.31E+03 2.93E+04 1.69E+04 NO DATA 2.10E+04 HO-99 NO DATA 2.48E+07 NO DATA 2.47E+07 4.84E+06 NO DATA 3.71E+07 NO DATA 8.18E+06 TC-99m 3.26E+00 6.73E+00 8.67E+01 NO DATA 7.24E+01 3.52E+00 1.96E+03 TC-101 3.26E-60 4.11E-60 4.06E-59 RU-103 NO DATA. 4.88E-59 2.24E-60 6.98E-58 1.04E+03 NO DATA 3.47E+02 NO DATA 2.16E+03 RU-105 9.60E-04 NO DATA 1.26E+04 NO DATA 3.23E-04 NO DATA 7.06E-03 NO DATA 3.82E-01 RU-106 2.28E+04 NO DATA 2.84E+03 NO DATA 2.69E+04 NO DATA 1.73E+05 AG-110m 4.62E+07 3.37E+07 2.23E+07 NO DATA 4.83E+07 NO DATA 1.75E+09 TE-125m 1.80E+07 6.02E+06 2.43E+06 6.06E+06 NO DATA NO DATA 8.58E+06
! TE-127m 5.04E+07 1.67E+07 6.10E+06 TE-127 1.46E+07 1.24E+08 NO DATA 2.03E+07 7.57E+02 2.54E+02 1.63E+02 6.16E+02 1.85E+03 TE-129m 6.68E+07 NO DATA 1.59E+04 2.29E+07 1.03E+07 2.57E+07 1.67E+08 TE-129 3.25E-10 ND DATA 3.99E+07 1.12E-10 7.59E-11 2.73E-10 8.10E-10 TE-131m 4.04E+05 1.63E+05 NO DATA 2.60E-08 1.34E+05 3.30E+05 1.12E+06 NO DATA 2.74E+06 TE-131 4.19E-33 1.55E-33 1.18E-33 3.74E-33 1.07E-32 NO DATA 1.69E-31 CLINTON-1 3-82 Rev.lS-7/97
CPS-ODCM TABLE 3.5-21 (continued) GOAT MILK PATHWAY FACTORS - Rh (INFANT) (m' mrem /yr per pCi/sec) ORGAN: BONE LIVER T. BODY THYROID KIDNEY _ LUNG' GI-LLI ISOTOPE TE-132 2.54E+06 1.26E+06 1.17E+06 1.85E+06 7.86E+06 NO DATA 4.65E+06 I-130 4.22E+06 9.28E+06 3.73E+06 1.04E+09 1.02E+07 NO DATA 1.99E+06 I-131 3.25E+09 3.83E+09 1.69E+09 1.26E+12 4.48E+09 NO DATA 1.37E+08 I-132 A.73E+00 3.50E+00 1.2SE+00 1.64E+02 3.91E+00 NO DATA 2.84E+00 I-133 4.34E+07 6.32E+07 1.85E+07 1.15E+10 7.43E+07 NO DATA 1.07E+07 I-134 1.97E-11 4.04E-11 1.44E-11 9.42E-10 4.52E-11 NO DATA 4.18E-11 I-135 1.36E+05 2.70E+05 9.85E+04 2.42E+07 3.01E+05 NO DATA 9.77E+04 CS-134 1.09E+11 2.04E+11 2.06E+10 NO DATA 5.25E+10 2.15E+10 5.54E+08 CS-136 5.92E+09 1.74E+10 6.50E+09 NO DATA 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 IA-140 4.83E+00 1.91E+00 4.90E-01 NO DATA NO DATA NO DATA 2.24E+04 LA-142 2.07E-11 7.60E-12 1.82E-12 NO DATA NO DATA NO DATA 1.29E-06 CE-141 5.20E+03 3.17E+03 3.73E+02 NO DATA 9.78E+02 NO DATA 1.64E+06 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 8.83E+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 P187 7.27E+03 5.06E+03 1.75E+03 NO DATA NO DATA NO DATA 2.97E+05 NP-239 4.37E+00 3.91E-01 2.21E-01 NO DATA 7.00E-01 NO DATA 1.13E+04 j
- mrem /yr per pCi/m 3 .
- 1.87 x 10' '
l i I CLINTON-1 3-83 Rev.lS-7/97
i 3dS-OG3H 1V8I'3 C*G-22 DOVI HI1M dVIHMVA g I:.V31 OHS - 8% )3HII'O( { )m maam/A2 da2 1 TDT / sad ( OHDVN: UON3 I'I A3H 1*UOGA 1HAUOIG NIGN3A I'nND DI-l'I'I IS01Od3 H-E NO QVIV C*203+0E. E*E03+0E. E*E03+OE, E*E03+00 E*203+OE, E*E03+OE. j 3-IF I'9G3+09 E*E63+OS. E*263+OS+ E*E63+OS, E*263+OS. E*Z63+09, E*263+OS, NV-ED I*OL3+09,, I*OL2+09 I*OL3+09 I*OL3+09 I*OL3+09 I*OL3+09 d-CZ I*OL3+09 6*EE3+IO
>*E93+06 E'S63+06 NO QVIV NO OVIV NO QVIV E*S83+06 _j l 3H-SI NO GY1V NO QVIV I*323+09 9*LL3+0E I'8S3+0E I*Et3+OP
) HN-SP 9*tL3+OS NO GY1Y 2*SI3+09 9*L03+OS NO GY1V L*053+OS NO GY1V 2*II3+09 HN-59 NO OVIV T*SE3-OE C*t93-09 NO QVIV I'8S3-0E NO QVIV 33-SS I*EI3-OI I I*PG3+09 L*9S3+OS Z*E03+OS NO QVIV NO QVIV t*ES3+OS I*&E3+OS { J3-S6 I*9S3+09 E*923+09 I*293+09 NO QV1V NO QVIV l L*E63+OS 2*923+09 30-98 NO GVIV I*t93+09 t*t93+09 NO GVIV NO UY1V NO GY1V 8*)63+09 30-90 NO QVIV S*I93+09 I*933+04 NO QVIV NO GY1V NO GY1V E'893+OL NI-9E E*SS3+06 I*603+08 I'ZI3+08 NO QVIV NO GYIV NO QVIV I*E03+OL j NI-99 I*663-OI I*063-02 I*063-OZ NO GY1V NO GY1V NO QVIV E*363+00 l 3n-9P NO GVIV 8*EE3+OE >*6L3+0E NO QVIV I*663+0t NO QVIV 2N-9S E*893+09 t*693+08 I*EE3+06 8*EE3+08 NO QVIV 8*EE3+08 NO QVIV E*EE3+08 2N-96 I*063-IE I'983-IE I*t93-IE NO QVIV 6*993-IE NO GY1V EH-8E 6*6t3-II NO QVIV NO GY1V NO QVIV NO QVIV NO QVIV NO QVIV NO GY1V EH-8P NO QVIV NO QVIV NO QVIV NO GY1V NO QVIV NO QVIV NO GV1Y { 3U-8S NO QVIV NO QVIV NO QVIV NO QVIV NO QVIV NO QVIV HH-89 NO GY1V l NO QVIV I*093+06 9*tL3+08 NO QVIV NO QVIV NO GY1V 9*LL3+OL HH-88 NO QVIV 8*963-t9 S*6L3-79 NO QVIV NO QVIV NO UY1V P*EI3-PL HH-06 NO OVIV I'9L3-SE I*t63-SE NO GY1V NO GVIV NO GVIV I*t93-SS bH-86 I*E63+IO NO QVIV E*693+08 NO QVIV NO QVIV NO GY1V S*EL3+08 I V-60 2*EG3+II NO QVIV S*693+IO NO QVIV NO QVIV NO GY1V E*I93+06 SH-6I E*LI3+OS NO GVIV I*023+09 NO QVIV NO GY1V NO GY1V S*663+OS SM-62 t*9I3+00 NO GVIV I'893-OI NO QVIV NO QVIV A-60 NO QVIV 8*Lt3+OI i E*893+01 NO GY1V I*0E3+00 NO QV1Y NO QVIV NO GVIV I I03+OS ! A-6Im E*tt3-20 NO QVIV I*ES3-ET NO QVIV NO QVIV NO QVIY 9*LE3-IL ) A-61 t'9L3+0E NO QVIV I*ES3+02 NO QVIV NO QVIV A-6E NO QVIV 9*223+0S C*033-0S NO QVIV 8*973-OL NO QVIV NO QVIV NO QVIV 8*LE3-OI A-6E I*303-0T NO GY1V E*363-0E NO QVIV NO GVIV 2U-6S NO QVIV I*L63+OE t'S83+0E I*OI3+OE 8*6L3+01 NO GY1V I*tt3+0E NO QVIV I*0S3+OS 2H-6L 2*E63-01 E*EI3-02 I*6S3-0E NO QV1Y t*L93-0E NO GY1V , S*033+OE ME-6S E*BI3+09 I*)83+09 I*093+09 NO QVIV I*E63+09 NO QVIV E*LS3+OL HO-66 NO QVIV 6*Lt3+09 2*tI3+09 NO QVIV E*083+OL 13-66m NO QVIV 8*0S3+09 I*983+00 E*I03+00 S*IE3+01 NO QVIV t*S03+01 I*SL3+00 I*L93+OE 13-101 I*993-90 I'9I3-90 E*093-96 NO QVIV un-10E E*Lt3-96 8*S02-91 S*II3-90 G*I03+0E NO QVIV I*693+0E NO QVIV I*E83+0E NO GY1V I*EE3+09 un-IOS t*SE3-09 NO QVIV I'9S3-09 NO-QVIV E*663-0E NO QVIV E*693-OI un-I09 I*II3+OP NO QVIV I*E03+0E NO QVIV yc tIom g*g03+04 I*)63+09 NO QVIV I*LE3+OS I*963+OL I*ES3+OL NO GY1V E*193+0L NO QVIV 3*OI3+06 13-IESW 8*893+09 E*E63+09 I*I83+09 Z*)83+09 NO GY1V NO QVIV I3-IgLm g*)63+OL 8*GE3+09 9'6I3+09 2*693+09 S*693+09 L*I03+OL NO GVIV 2*023+OL 13-IEL E*St3+OE 6*9I3+01 L*993+01 E*PL3+02 I*OI3+0E 13-IE6m E*Et3+OL NO,GY1V I*E63+09 6*093+09 S*0E3+09 I*OS3+OL 6*933+0L NO QVIV E*693+0L 13-136 I*SE3-10 t*283-II E'993-II I*063-IO >*)63-I0 NO QVIV 6*9S3-06 13-IgIm I*613+OS 9*903+0t L*033+0t I*E93+OS 9'E63+OS NO QVIV 2*983+09 13-IEI I*693-EE S*643-EP S'8E3-EP I*S02-EE S*623-EE NO GVIV I*0E3-EZ 31 INION-I E-8# d 'L L/ L i
y 1 l l l CPS-ODCM TABLE 3.5-22 (continued) l GOAT MILK PATHWAY FACTORS - Rh (CHILD) (m' mrem /yr per pCi/sec) l ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI
- ISOTOPE
'TE-132 1.23E+06 5.45E+05 6.59E+05 7.94E+05 5.06E+06 NO DATA 5.49E+06
-130 2.06E+06 4.17E+06 2.15E+06 4.59E+08 6.23E+06 NO DATA 1.95E+06
!I-131 1.56E+09 1.57E409 8.94E+08 5.20E+11 2.58E+09 NO DATA 1.40E+08
- I-132 8.32E-01 1.52E+00 7.03E-01 7.09E+01 2.34E+00 NO DATA 1.80E+00
- I-133 2.06E+07 2.55E+07 9.64E+06 4.73E+09 4.25E+07 NO DATA 1.03E+07
!I-134 9.51E-12 1.77E-11 8.13E-12 4.06E-10 2.70E-11 NO DATA 1.17E-11
- I-135 6.53E+04 1.17E+05 5.56E+04 1.04E+07 1.80E+05 NO DATA 8.95E+04 i 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 NO 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 I BA-139 2.42E-08 1.29E-11 7.01E-10 NO DATA 1.13E-11 7.59E-12 1.40E-06 !BA-140 1.40E+07 1.22E+04 8.15E+05 NO DATA 3.98E+03 7.29E+03 7.07E+06 BA-141 2.34E-46 1.31E-49 7.62E-48 NO DATA 1.13E-49 7.70E-49 1.33E-46
- BA-142 1.31E-80 9.44E-84 7.32E-82 NO DATA 7.64E-84 5.55E-84 1.71E-82
,LA-140 2.32E+00 8.12E-01 2.53E-01, NO DATA NO DATA NO DATA 2.26E+04
- LA-142 9.85E-12 3.14E-12 9.83E-13 NO DATA NO DATA NO DATA 6.22E,07 CE-141 2.62E+03 1.31E+03 1.94E+02 NO DATA 5.73E+02 NO DATA 1.63E+06 CE-143 2.24E+01 1.22E+04 1.76E+00 NO DATA 5.10E+00 NO DATA 1.78E+05 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 9.29E+04
- PR-144 3.53E-54 1.09E-54 1.78E-55 1:0 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
-187 3.46E+03 2.05E+03 9.20E+02 NO DATA NO DATA NO DATA 2.88E+05 NP-239 2.07E+00 1.49E-01 1.04E-01 NO DATA 4.29E-01 NO DATA 1.10E+04 l
i*mrtm/yr per pCi/m3 -
- 1.07 x 10' l
l l l pLINTON-1 3-85 Rev.15-7/97
3dS-OODW 1V813 C*9-2E DOVI Hill > dVIHMVA 3VD1OUS - B 3 '"I )133N( g
)m maam/42 daJ liDT (
OUDVN: GON3 1*GOGA 1HAHOIG I'IASE iDGN3A I'nND DI-ITI IS01Od3 H-0 NO OVIV 2*023+0E, Z*023+OE* Z*023+OE* 2*023+0E. 2*023+0E. Z*023+0E. 3-IP 9*L03+OS. I*Et3+OS. I*Et3+OS, I*ED3+OS. I*Et3+OS. I*Et3+OS. I*Et3+OS, NV-ED S*IS3+OS,, S*IS3+OS S*IS3+OS S*IS3+OS S*IS3+OS S*IS3+OS S*IS3+OS d-EZ C*L83+IO Z*ED3+06 I*PL3+06 NO GY1V NO GV1V NO QVIV C*I83+06 3H-SI NO QVIV NO QVIV G*6P3+0E E*E03+0E I*E03+0E 8*)83+0E HN-SD NO QVIV 6*683+OS I*983+09 E*EZ3+OS NO QVIV S*003+OS NO GY1V E*t)3+09 HN-59 NO GVIV 8*LL3-ot I'993-0# NO QVIV 33-SS I*II3-OE NO QVIV S*LL3-02 G*L63+OS t*II3+09 6*SL3+OP NO QVIV NO QVIV Z*903+OS J3-S6 9*LG3+OS I*t83+OS I*S03+09 9*083+0S NO QVIV NO QVIV t*6L3+OS C*LE3+09 30-S8 NO QVIV 6*SI3+OG Z*I63+09 NO QVIV NO QVIV NO QVIV I*EI3+OL 30-90 NO GV1V C*EZ3+09 L*tL3+09 NO QVIV NO QVIV NO QVIV )*EZ3+OL NI-9E I*)33+06 I*003+08 t*8I3+OL NO QVIV NO QVIV NO QVIV I*903+OL NI-9S 8*063-02 I*0E3-02 P*LI3-OC NO GVIV NO QVIV NO QVIV S'913-OI 3n-9# NO QVIV t'983+0E E'Z03+OE NO GY1V I*I83+09 NO QVIV ZN-9S Z*SE3+08 E'9E3+OS 8*L93+08 t*063+08 NO QVIV S*9I3+00 NO QVIV E*LI3+08 2N-96 t*tt3-IE 8*t93-IE S*622-ID NO QVIV S*SE3-IE 2H-8E NO GY1V I*993-IZ NO QVIV NO QVIV NO QVIV NO QVIV NO QVIV NO QVIV JH-89 NO GY1V NO GVIV NO QVIV NO QVIV NO UVIV NO QVIV NO UY1V HH-8S NO GY1V NO QVIV NO GVIV NO QVIV NO GYIV NO QVIV NO QVIV UE-89 MO QVIV NO QVIV S*993+00 2*993+00 NO QVIV NO QVIV NO GY1V 8*E83+0L HG-88 NO QVIV t*993-)9 Z*t83-t9 NO QVIV NO QVIV NO QVIV E*663-SE HH-86 NO QVIV 6*SZ3-SP 9*LE3-SP NO GY1V NO QVIV NO QVIV I*t93-92 sE-86 S*963+06 NO QVIV I*903+08 NO QVIV NO QVIV NO QVIV
)-60 I*E03+TI 9'9S3+08 NO GY1V E*t03+IO NO QVIV NO QVIV NO QVIV E'843+06 SH-61 I*II3+OS NO QVIV t*>03+0E NO QVIV NO QVIV NO QVIV S*0I3+0S SU-62 I*863+00 NO QVIV 8*OS3-02 NO QVIV NO QVIV NO GY1V t*8I3+OI A-60 I*S93+OI NO QVIV t'ZI3-OT NO GY1V NO QVIV NO GYIV I*363+OS A-6 tru I*tI3-ZO NO QVIV S*EL3-ZZ NO QVIV A-61 NO QVIV NO QVIV 9*9t3-16 I*863+0E NO GVIV S*OL3+OI NO QVIV NO QVIV NO QVIV A-62 I'ZE3-0S L*LS3+0S NO QVIV E*SL3-OL NO QVIV NO QVIV NO QVIV E E63-OI A-6E t*893-02 NO QVIV I*EE3-OE NO QVIV 2U-6S NO QVIV NO QVIV I*t63+0E I*683+OZ 9*3t3+OI t*263+OI NO QVIV 6'It3+OI NO GYIV I*tt3+0S 2H-6L 6*tE3-02 I'8L3-02 8 903-OE NO UY1V NO QVIV ,, S*0S3+0E Z*8E3-OZ NG-6S I*963+ot 6*EL3+0E S I93+0E NO UY1V HO-66 6*083+0E NO GVIV t*OI3+OL NO QVIV S*EE3+09 I*023+09 NO QVIV I'ZZ3+OL 13-66m 9*8L3-OI NO QVIV 6 993+09 I*623+00 Z*t83+OI NO QVIV Z*893+01 I*093+00 I'Z93+OE 13-I0I 9*293-91 8*613-91 8*L93-90 NO QVIV I'9I3-S6 S*tE3-91 I*S23-9L un-IDE Z'It3+02 NO QVIV 6*3L3+01 NO QVIV L*973+02 un-IOS NO QVIV I*OI3+09 I*893-09 NC GY1V L ZI3-0S NO QVIV Z*ES3-OE NO QVIV I*S03-01 un-I09 t*tL3+0E NO QVIV S*9E3+02 NO GY1V 8*923+0E NO QVIV 2*Ip3+OS VD-110m I*IS3+OL I*063+OL 9*923+09 NO QVIV 13-IZSW Z*083+OL NO GY1V E*093+06 E*S62+09 I*363+09 t*803+OS I*003+09 NO GY1V 13-TELW NO QVIV I*093+OL I*0I3+0L C*SL3+09 I*203+09 Z*E63+09 t*003+OL NO OVIV Z*SI3+OL 13-IZL I*t83+OZ S*It3+01 E*I83+OI I*023+02 S'8L3+02 NO GY1V 13-IE6m I*EE3+OL I*It3+09 t*863+09 Z*003+09 )*ES3+09 S*S13+OL NO GY1V t*6t3+OL 13-IZ6 9'223-II Z*EE3-II I*St3-II t tt3-II Z*9I3-10 NO GVIV E*t03-IO
' 13-IEIW L*893+01 C*Lt3+0t E*It3+09 S'9L3+OP E*6E3+OS i NO QVIV E*023+09 13-IEI 8*093-ED C*E13-EP Z*SI3-EP 9'I63-ED E*SI3-EE NO QVIV 9"903-ES 3qINION-I C-89 80^'IS-L/6L
CPS-ODCM TABLE 3.5-23 (continued) GOAT MILK PATHWAY FACTORS - R".y (TEEN) (m2 mrem /yr per Ci/sec) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE TE-131 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+08 9.01E+08 4.84E+08 2.63E+11 1.55E409 NO DATA 1.78E+08. I-132 3.52E-01 9.20E-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 I-135 2.75E+04 7.08E+04 2.62E+04 4.56E+06 1.12E+05 NO DATA 7.85E+04 CS-134 2.94E+10 6.91E+10 3.21E+10 NO DATA 2.20E+10 8.39E+09 8.60E+08 C5-136 2.34E+09 5.27E+09 3.54E+09 NO DATA 2.87E+09 4.52E+08 4.24E+08 C5-137 4. 0'15+10 5.33E+10 1.86E+10 NO DATA 1.82E+10 7.05E+09 7.59E+08 CS-138 4.73E-23. 9.08E-23 4.54E-23 NO DATA 6.70E-23 7.80E-24 4.12E-26 BA-139 9.84E-09 6.92E-12 2.87E-10 NO DATA 6.53E-12 4.77E-12 8.78E-08 BA-140 5.82E+06 7.13E+03 3.75E+05 NO DATA 2.42E+03 4.80E+03 8.98E+06 BA-141 9.53E-47 7.11E-50 3.18E-48 NO DATA 6.60E-50 4.87E-50 2.03E-52 BA-142 5.44E-81 5.44E-84 3.35E-82 NO DATA 4.60E-84 3.62E-84 1.67E-92 LA-140 9.67E-01 4.75E-01 1.26E-01 NO DATA NO DATA NO DATA 2.73E+04 LA-142 4.08E-12 1.81E-12 4.51E-13 NO DATA NO DATA NO DATA 5.52E-08 CE-141 1.07E+03 7.12E+02 8.17E+01 NO DATA 3.35E+02 NO. DATA 2.04E+06 CE-143 9.14E+00 6.65E+03 7.43E-01 NO DATA 2.98E+00 NO DATA 2.00E+05 CE-144 7.86E+04 3.25E+04 4.23E+03 NO DATA 1.94E+04 NO DATA 1.98E+07 PR-143 3.47E+01 1.39E+01 1.73E+00 NO DATA 8.06E+00 NO DATA - 1.14E+05 PR-144 1.42E-54 5.81E-55 7.19E-56 NO DATA 3.33E-55 NO DATA 1.56E-57 MD-147 2.17E+01 2.36E+01 1.41E+00 NO DATA 1.38E+01 NO DATA 8.50E+04 1-187 1.43E+03 1.165+03 4.08E+02 NO DATA No DATA NO DATA 3.15E+05 NP-239 8.38E-01 7.90E-02 4.39E-02 NO DATA 2.48E-01 NO DATA 1.27E+04
- mrem /yr per pC1/m 3
- 5.15 x 10' I
l CLINTON-1 3-87 Rev.15-7/97
3dS-OGOH 1V81'3 C
- G-2 &
DOVI NI7M dVIHMVA 3VO1 OHS - H% )V0nI'l(
)m,lu2.am/ AJ daJ iroT / sac (
OHDYN: GON3 I'I A3H 1*GOGA 1HAHOIG ID GN3A 1YfND DI-ITI IS01Od3 H-E NO OVIV I'993+0E. I'SS3+0E* E'9E3+OS, I'993+0E. I*SS3+0E. I*SS3+OE, I*SS3+00+ 3-Ik L*293+0t. L*E93+0t. L*393+0>. L*293+0t. L*293+0t, L*393+09, MV-EP Z*693+OS,, 2'6S3+OS 2*6S3+0S 2*653+0S 2*6S3+OS 2*6S3+OS Z*693+OS d-CZ Z*OS3+IO I'2L3+06 L*6I3+08 NO GVIV NO QVIV NO OVIV Z*E03+06 3U-SI NO QVIV NO QVIV E*PE3+0E 2*053+0E L*S93+02 HN-SP )*SS3+0E 8*9E3+OS NO GY1V I*OI3+09 I*623+OS NO QVIV 2*663+09 HN-99 NO QVIV E*083+09 NO OVIV t*693-OP 8*L63-0S NO OVIV 9*263-OP 32-SS NO QVIV I'993-OZ E'ZL3+OS 2*293+OS G*EL3+09 NO GV1V NO OVIV J3-S6 E*8S3+OS I*E93+0S I*E03+OS 6*093+OS E'PL3+OS NO QV1Y NO QVIV 2*SE3+OS 30-98 NO GY1V E*0E3+09 S*923+OS I*Z93+09 NO QVIV NO OVIV NO GV1Y I*I>3+OL 30-90 NO QVIV I*693&09 t EE3+09 NO QVIV NO QVIV NO QVIV E'963+OL NI-9E 8*053+08 S'S83+OL Z*L03+OL NO GYIV NO QVIV NO QVIV I*193+OL NI-9S >*DE3-02 9*L93-OC 2*9E3-OE NO GY1V NO OVIV 3n-99 NO QVIV I*t93-01 NO QVIV Z'933+0E I*EE3+0E NO GV1Y 9*9Z3+0E NO QVIV E'Zt3+OS 2H-9S I'9t3+08 S*223+08 Z*F93+08 NO QVIV E'F63+00 NO QVIV 2N-96 Z*tI3-IE E*E63+08 t'913-IE C*EI3-IW NO QVIV C*003-IC NO QVIV 9*6E3-IP HH-BE NO QVIV NO GVIV NO UVIV NO QVIV 2H-8P NO QVIV NO QVIV NO QVIV NO QVIV NO QVIV NO UY1V NO QVIV NO GY1V TH-89 NO QV1Y NO GVIV NO OVIV NO QVIV NO UVIV NO UVIV NO GY1V HH-89 NO GY1V NO QVIV NO GVIV E*T03+08 I*t93+09 NO GVIV NO QVIV NO UY1V 9'IZ3+OL ME-88 NO QVIV 3*SL3-t9 I*E93-t9 NO QVIV NO QVIV NO GY1V E*SS3-SL H8-86 NO QVIV G*EL3-GP E'L83-SP NO GVIV bH-86 NO QVIV NO GY1V E*IZ3-9L C*093+06 NO QVIV 8'LE3+04 NO QVIV NO QVIV 1-60 6*L83+IO NO GYIV NO QVIV )*883+00 Z*t03+TO NO GY1V NO QVIV NO QVIV Z*8E3+06
- f H-6I 9*OI3+0t NO QVIV 2*tE3+0E NO QVIV SH-6E NO GYIV NO OVIV Z*893+OS I*0E3+00 NO QVIV t*t93-OZ NO QVIV NO OVIV A-60 8*)83+00 NO QVIV E*0t3+OI NO QVIV E*.383-01 NO QVIV NO GY1V NO QVIV A-6Im t'963-ZI 6*003+07 NO OVIV Z*683-32 NO GVIV NO QVIV NO QVIV A-6I I*0E3+OE NO UYIV E*393-ZO E*493+01 NO UVIV NO UVIV NO QVIV S*993+09 A-63 9*993-09 NO QVIV I*6S3-OL NO QVIV A-6E NO QVIV NO QVIV I*It3-OI E'9S3-OZ NO OVIV L*EZ3-09 NO OVIV NO OVIV 2H-69 I*IE3+02 NO OVIV 8*tI3+02 E'9E3+OI Z*t93+OI .NO QVIV S'963+01 2H-6L S*IL3-OZ I*0t3-OZ NO GY1V , I*IS3+09 t*LL3-OE NO QVIV I*S83-02 NO QV1Y E*EE3+0E NG-69 6*603+0E 9*913+0E 2*693+0E NO UVIV 9*>93+0E NO GV1Y E*E)3+OL HO-66 NO GVIV E*693+09 9*9E3+09 NO UVIV 9*LI3+09 NO GY1V 9*893+09 13-66M E*693-01 I I33+00 I'>33+01 NO QVIV 13-101 I*L03+01 9*tt3-01 9'913+OJ-E'tE3-91 >*6t3-91 t'893-90 NO UY1V 8*863-90 un-IOC I*223+02 NO UY1V 2*923-91 I*t83-LZ S'Et3+0T NO QVIV >*9t3+02 NO QVIV I*)33+09 un-IOS I*0Z3-09 NO GY1V t*033-0S NO QVIV I*C23-OE NO GY1V 9*gE3-02 un-I09 Z*t)3+0E NO QVIV C*063+02 NO QVIV t*L23+0E ys-II0m 9*693+09 NO QVIV I*983+09 2g-tggm 9*tt3+09 E'823+09 NO QVIV I'ZL3+OL NO QVIV E'9E3+06 I*6S3+09 l*OL3+OS E'913+OS G*8L3+OS L*6t3+09 13-IZLm S*y93+09 NO QVIV L*L63+09 I*693+09 9'993+0S I*>03+09 2*223+OL NO OVIV 13-IZL L*823+01 E*8I3+OI I'963+01 S'803+OI Z*8E3+9l 13-1Z65 C*163+02 NO QVIV 9'It3+0E t*ZI3+09 E'963+09 I*It3+09 2*t83+09 E*OI3+OL NO.GVIV 13-IZ6 E'9E3+OL E'8E3-II I'Z03-II 8'ZE3-IZ Z*963-II I't23-IO NO QVIV 13-IEIW )*EE3+0t Z*IE3+ot I'L93+0t E'ES3+OP 2*993-11 E*It3+OS NO QVIV E'I03+09 13-IEI t'EL3-EP I'8E3-EP I*E83-EP E'903-EP I*623-EE NO QVIV 9*163-ES 31 INION-I E-88 BBA*L9-L/6L,
1 l CPS-ODCM l TABLE 3.5-24 (continued) GOAT MILK PATHWAY FACTORS - R'.y (ADULT) (m mrem /yr per pCi/sec) 2 ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI , ISOTOPE (E-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 I-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 1.85E+01 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 I-134 2.27E+12 6.16E-12 2.20E-12 1.07E-10 9.80E-12 NO DATA 5.37E-15 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 3.54E-12 2.15E-12 9.44E-09 i 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 DATA 3.64E-50 2.22E-50 2.44E-56 f BA-142 3.00E-81 3.09E-84 1.89E-82 NO DATA 2.61E-84 1.75E-84 4.23E-99 I 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 1.82E+02 NO DATA 1.50E+06 CE-143 5.00E+00 3.70E+03 4.09E-01 NO DATA 1.63E+00 NO DATA 1.38E+05 CE-144 4.29E+04 1.79E+04 2.30E+03 NO DATA 1.06E+04 NO DATA 1.45E+07 PR-143 1.89E+01 7.56E+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 ND-147 1.13E+01 1.30E+01 7.79E-01 NO DATA 7.64E+00 NO DATA 6.25E+04
' 187 7.78E+02 6.50E+02 2.27E+02 NO DATA NO DATA NO DATA 2.13E+05 HP-239 4.39E-01 4.32E-02 2.38E-02 NO DATA 1.35E-01 NO DATA 8.86E+03
- mrem /yr per 6 pCi/m'
**2.95 x 10 i
FT.T NTON- 1 .3-89 Rev.15-7/97 j
CPS-ODCM TABLE 3.5-25 i MEAT PATHWAY FACTORS - RS3 (CHILD) (m* mrem /yr per pCi/sec) { ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG ISOTOPE GI-LLI H-3 NO DATA 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* 2.33E+02* NA-24 1.06E+05* 1.06E+05* 1.06E+05*. 1.84E-03** 1.84E-03 1.84E-03 1.84E-03 1.84E-03 P-32 7.43E+09 1.84E-03 1.84E-03 3.47E+08 2.86E+08 NO DATA NO DATA CR-51 NO DATA NO DATA 2.05E+08 NO DATA 8.78E+03 4.88E+03 1.33E+03 i HN-54 NO DATA 8.90E+03 4.66E+05 ' 8.03E+06 2.14E+06 NO DATA 2.2SE406 NO DATA HN-56 NO DATA 1.56E-53 3.52E-54 6.74E+06 NO DATA 1.89E-53 NO DATA FE-55 4.58E+08 2.43E+08 7.52E+07 2.26E-51 FE-59 NO DATA NO DATA 1.37E+08 4.50E+07 3.76E+08 6.09E+08 3.03E+08 NO DATA CO-58 NO DATA 1.76E+08 6.34E+08 NO DATA 1.64E+07 5.03E+07 NO DATA CO-60 NO DATA NO DATA 9.58E+07 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 I NO DATA NO DATA 1.05E+08 NI-65 3.55E-52 3.34E-53 1.92E-53 NO DATA NO DATA CU-64 NO DATA NO DATA 4.10E-51 2.77E-07 1.67E-07 NO DATA 6.69E-07 ZN-65 3.75E+08 NO DATA 1.30E-05 1.00E+09 6.22E+08 NO DATA 6.30E+08 ZN-69 0.00E+00 NO DATA 1.'76E+08 0.00E+00 0.00E+00 NO DATA 0.00E+00 BR-83 NO DATA NO DATA NO DATA 0.00E+00 NO DATA NO DATA NO DATA NO DATA BR-84 NO DATA NO DATA NO DATA NO DATA , NO DATA NO DATA NO DATA NO DATA BR-85 NO DATA NO DATA NO' DATA RB-86 NO DATA NO DATA NO DATA NO DATA NO DATA 5.76E+08 3.54E+08 NO DATA _RB-88 NO DATA NO DATA NO DATA 3.71E+07 0.00E+00 0.00E+00 NO DATA NO DATA RB-89 NO DATA NO DATA 0.00E+00 0.00E+00 0.00E+00 NO DATA NO DATA
' -89 4.00E+08 NO DATA NO DATA 0.00E+00 1.37E+07 NO DATA NO DATA NO DATA 3-90 1.04E+10 NO DATA 2.64E+09 1.86E+07 NO DATA NO DATA NO DATA 1.40E+08 SR-91 2.26E-10 NO DATA 8.53E-12 NO DATA NO DATA NO DATA SR-92 2.00E-49 NO DATA 8.04E-51 4.99E-10 Y-90 NO DATA NO DATA NO DATA 3.80E-48 1.73E+02 NO DATA 4.62E+00 NO DATA Y-91m NO DATA NO DATA 4.91E+05 0.00E+00 NO DATA 0.00E+00 NO DATA Y-91 1.80E+06 NO DATA NO DATA 0.00E+00 NO DATA 4.81E+04 NO DATA NO DATA Y-92 2.37E-39 NO DATA NO DATA 2.40E+08 6.78E-41 NO DATA NO DATA NO DATA 6.84E-35 Y-93 6.98E-12 NO DATA 1.92E-13 ZR-95 NO DATA NO DATA NO DATA 1.04E-07 2.67E+06 5.87E+05 5.22E+05 NO DATA ZR-97 3.16E-05 8.40E+05 NO DATA 6.12E+08 4.57E-06 2.69E-06 NO DATA 6.55E-06 NB-95 3.10E+06 NO DATA ' 6.92E-01 1.21E+06 8.61E+05 NO DATA 1.13E+06 HO-99 NO DATA 1. '.4 E+05 NO DATA 2.23E+09 TC-99m 2.83E+04 NO DATA 2.44E+05 No DATA 6.01E-21 1.-8E-20 1.95E-19 9.45E+04 NO DATA 1.71E-19 5.98E-21 6.71E-18 TC-101 0.00E+00 0.00E+00 0.00E+00 RU-103 NO DATA 0.00E+00 0.00E+00 0.00E+00 1.55E+08 NO DATA 5.96E+07 NO DATA RU-105 8.48E-28 NO DATA 3.90E+08 NO DATA 4.01E+09 3.08E-28 NO DATA 7.45E-27 RU-106 4.43E+09 NO DATA 5.53E+08 NO DATA 5.54E-25 AG-110m NO DATA 5.99E+09 NO DATA 6.90E+10 8.41E+06 5.68E+06 4.54E+06 NO DATA TE-125m 5.69E+08 1.06E+07 NO DATA 6.75E+08 1.54E+08 7.5BE+07 1.60E+08 NO DATA TE-127m 1.77E+09 NO DATA 5.49E+08 4.78E+08 2.11E+08 4.24E+0B 5.06E+09 TE-127 3.34E-10 9.01E-11 7.17E-11 NO DATA 1.44E+09
_TE-129m 1.79E+09 2.31E-10 9.51E-10 NO DATA 1.31E-08 4.99E+08 2.77E+08 5.76E+08 5.25E+09 TE-129 0.00E+00 0.00E+00 0.00E+00 NO DATA 2.18E+09 TE-131m 0.00E+00 0.00E+00 NO DATA 0.00E+00 6.97E+02 2.41E+02 2.57E+02 4.96E+02 .TE-131 0.00E+00 0.00E+00 2.33E+03 No DATA 9.78E+03 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 T-
CPS-ODCM TAIEE 3. 5-25 (continued) MEAT PATHWAY FACTORS - R*m (CHILD) (m# mrem /yr per pCi/sec) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE 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 1-134 0.00E+00 0.00E400 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 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 j CS-137 1.33E+09 1.27E+09 1.88E+08 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 BA-139 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 0.00E+00 0.00E+00 BA-140 4.30E+07 3.84E+04 2.56E+06 NO DATA 1.25E+04 2.29E+04 2.22E+07 BA-141 0.00E+00 0.00E400 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 j LA-140 5.56E-02 1.94E-02 6.05E-03 NO DATA NO DATA NO DATA 5.41E+02 LA-142 6.18E-92 1.97E-92 6.17E-93 NO DATA NO DATA NO DATA 3.91E-87 CE-141 2.22E+04 1.11E+04 '1.64E+03 NO DATA 4.85E+03 NO DATA 1.38E+07 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 PR-143 3.34E+04 1.00E+04 1.66E+03 NO DATA 5.43E+03 NO DATA 3.60E+07
)
PR-144 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 NO DATA 0.00E+00 l
*0-147 1.17E+04 9.47E+03 7.33E+02 NO DATA 5.20E+03 NO DATA 1.50E+07 -187 3.21E-02 1.90E-02 8.53E-03 NO DATA NO DATA NO DATA 2.67E+00 NP-239 4.23E-01 3.04E-02 2.14E-02 NO DATA 8.79E-02 NO DATA 2.25E+03
- mrtm/yr per pCi/m 3
- 1.84 x 10-'
m mena 7-41 Rev.15-7/97
CPS-ODCM TABLE 3.5-26 i MEAT PATHWAY FACTORS - R* q (TEEN) (m# mrem /yr per Ci) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE H-3 NO DATA 1.93E+02* 1.93E+02* 1.93E+02* 1.93E+02* 1.93E+02* C-14 1.93E+02* 2.81E+05* 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 P-32 1.16E-03 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 MN-54 9.50E+05 NO DATA 7.02E+06 1.39E+06 NO DATA 2.09E+06 NO DATA 1.44E+07 HN-56 NO DATA 1.17E-53 2.09E-54 NO DATA 1.48E-53 FE-55 NO DATA 7.72E-52 2.30E+08 1.69E+08 3. 94 E+07 - NO DATA NO DATA 1.07E+08 7.31E+07 FE-59 2.12E+0B 4.95E+08 1.91E+08 NO DATA NO DATA 1.56E+08 CO-58 1.17E+09 NO DATA 1.41E+07 3.25E+07 NO DATA NO DATA NO DATA CO-60 1.94E+08 NO DATA 5.84E+07 1.32E+08 NO DATA NO DATA NO DATA 7.61E+08 NI-63 1.52E+10 1.07E+09 5.15E+08 NO DATA NO DATA NO DATA 1.71E+08 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 ZN-65 2.50E+08 NO DATA 1.60E-05 8.69E+08 4.05E+08 NO DATA 5.56E+08 NO DATA 3.68E+08 ZN-69 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 NO DATA BR-83 PO DATA 0.00E+00 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA
*R-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 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 RB-89 NO DATA 0.00E+00 NO DATA 0.00E+00 0.00E+00 NO DATA NO DATA NO DATA 2.54E+08 0.00E+00
'.-89 NO DATA 7.27E+06 NO DATA NO DATA NO DATA 3.02E+07
.-90 8.04E+09 NO DATA 1.99E+09 NO DATA NO DATA NO DATA 2.26E+08 SR-91 1.20E-10 NO DATA 4.78E-12 NO DATA SR-92 1.08E-49 NO DATA NO DATA 5.45E-10 l NO DATA 4.59E-51 NO DATA NO DATA NO DATA 2.74E-48 i Y-90 9.11E+01 NO DATA 2.45E+00 NO DATA NO DATA Y-91m NO DATA 7.51E+05 0.00E+00 NO DATA 0.00E+00 NO DATA NO DATA NO DATA 0.00E+00 Y-91 9.55E+05 NO DATA 2.56E+04 NO DATA Y-92 NO DATA NO DATA 3.91E+08 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 1.13E-07 ER-95 1.50E+06 4.74E+05 3.25E+05 NO DATA 6.93E+05 NO DATA 1.09E+09 ER-97 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 MO-99 NO DATA 4.25E+09 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 6.26E-18 TC-101 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 RU-103 0.00E+00 0.00E+00 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 RU-106 2.36E+09 NO DATA 2.97E+08 NO DATA 4.54E+09 NO DATA 1.13E+11 AG-110m 5.04E+06 4.77E+06 2.90E+06 NO DATA TE-125m 9.10E+06 NO DATA 1.34E+09 3.03E+08 1.09E+08 4.06E+07 8.47E+07 NO DATA NO DATA 8.95E+08 TE-127m 9.40E+08 3,33E+08 1.12E+08 2.24E+08 TE-127 3.81E+09 HO DATA 2.34E+09 1.78E-10 6.30E-11 3.82E-11 1.23E-10 7.20E-10 NO DATA 1.37E-08 TE-129m 9.49E+08 3.52E+08 1.50E+08 3.06E+08 3.97E+09 NO' DATA 3.56E+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 3.73E+02 1.79E+02 1.49E+02 2.69E+02 1.87E+03 TE-131 0.00E+00 NO DATA 1.44E+04 0.00E+00 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 CLINTON-1 3-92 nmr 14-7/07
CPS-ODCM TABLE 3.5-26 (continued) MEAT PATHWAY FACTORS - R",o (TEEN) 1 (m# mrem /yr per pCi/sec) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE TE-132 1.17E+06 7.38E+05 6.95E+05 7.78E+05 7.08E+06 NO DATA 2.34E+07 I I-130 1.63E-06 4.71E-06 1.88E-06 3.84E-04 7.2SE-06 NO DATA 3.62E-06 l I-131 0.89E+06 1.24E+07 6.69E+06 3.63E+09 2.14E+07 NO DATA 2.46E+06 I-132 5.78E-59 1.51E-58 5.42E-59 5.09E-57 2.38E-58 NO DATA 6.58E-59 - I-133 3.09E-01 5.2SE-01 1.60E-01 7.32E+01 9.20E+01 NO DATA 3.97E-01 1 I-134 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 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. 4 95!;+ 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 O.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 IA-140 3.03E-02 1.49E-02 3.97E-03 NO DATA NO DATA NO DATA 8.56E+02 IA-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 3.04E+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
*D-147 6.22E+03 6.76E+03 4.05E+02 NO DATA 3.97E+03 NO DATA 2.44E+07 -187 1.74E-02 1.42E-02 4.96E-03 NO DATA NO DATA NO 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
* *1.16 x 10-3 l
l l 1 i l CLINTON-1 3-93 Rev.15-7/97
3dS-OGDH-1V813 C*G-2L l H3VI dVIHMVA 3VD1OUS - U% )VG071(
)W WJOW/ AJ daJ liDT / SOD (
OHDVNI SON 3 I'I A3H 1*GOGA 1HAUOIG XIGN3A I'nND DI-ITI IS01Od3 H-E NO GVIV E*2t3+02, C*2t3+02 E*2t3+OE, E*2t3+0Z, E*2t3+02 E*293+02 3-IP E*EE3+OS, 9*993+0t. 9*993+0>. 9*993+0k, 9*993+0t, 9*993+09, 9*993+09, NY-EP I*tS3-OE,, I*tS3-OE I*tS3-OE I*tS3-OE I*tS3-OE I*PG3-OE I*tS3-OE d-EZ t'9G3+06 2*863+08 I'803+08 NO GVIV NO GVIV NO QVIV S*EE3+08 3H-SI NO GYIV NO GY1V L*053+0E t*EI3+0E I*SS3+0E. 6*EG3+0E I'LL3+09 NN-GP NO GY1V 6*I63+09 I*LS3+09 NO QVIV Z*LE3+09 NO OVIV E'8I3+OL NN-59 NO OVIV I't93-SE 2*SL3-GP NO OVIV I*893-SE NO OVIV t*923-92 l J2-SS Z*6)3+08 E*0E3+08 t*Et3+OL NO GVIV NO UVIV I*IE3+08 I*IL3+08 J2-56 E'992+08 *9*Et3+08 E*E63+08 NO GY1V NO QVIV I'Lt3+08 E*083+06 30-58 NO GVIV I*8E3+0L >*063+OL NO GY1V NO GY1V NO OVIV E*L02+08 30-90 NO OVIV L*SI3+OL I'993+08 NO UVIV NO QVIV NO UY1V I*PT2+06 NI-9E I*863+IO I*EI3+06 9*EE3+08 NO UY1V NO UVLY - NO OVIV E*LE2+09 NI-9$ E*EL2-SE E*692-SE I*Et2-SE NO OVIV NO UVIV NO UVIV L*t92-SE 3n-99 NO UVIV E*SE3-OL I*I82-OL NO UVIV 9*E92-OL NO UVIV Z*IS3-0S 2N-9S E'992+08 I*IE2+06 S*IE2+08 NO UVIV L*SL3+09 NO UVIV L*IE2+08 2N-96' O*002+00 0*002+00 0*002+00 NO UVIV O*002+00 NO UVIV O*002+00 3H-8E NO UVIV NO UVIV NO UVIV NO UVIV NO OVIV NO UVIV NO UVIV SM-9t NO UVIV NO UVIV NO U#'1V NO QVIV NO UVIV NO UVIV NO UVIV , SM-8S NO UVIV NO UVIV NO UVIV NO UVIV NO UVIV NO UVIV NO UW1V H9-89 NO UVIV t*8L3+08 E*EL2+09 NO UVIV NO UVIV NO UVLY 6*912+OL MS-88 NO UVIY 0*002+00 O*002+00 NO UVIV NO UVIV NO UVIV O*002+00 UE-86 NO UVIV 0*002+00 O*002+00 NO QVIV NO UVIV NO OVIV 0'002+00 L-86 E*0I2+08 NO QVIV 8*9)3+09 NO UVIV NO UVIV NO UVIV t*8E2+OL
*-60 I*Et3+IO NO UVIV E*092+06 NO UVIV NO UVIV NO QVIV E*S62+08 SM-6I I*PE2-IO NO UVIV G*L62-IE NO UVIV NO UVIV NO QVIV 9 8C3-IO sH-6E I*E82-96 NO UVIV S*992-91 NO UVIV NO UVIV NO UVIV E*992-98 l
A-60 I*063+OE NO UVIV E*6E2+00 NO UVIV NO QVIV NO UVIV I*IS2+09 A-6IW 0*002+00 NO UVIV 0*002+00 NO UVIV NO UVIV NO UVIV O*002+00 A-61 I*IE2+09 NO UVIV E*0E2+07 NO QVIV NO QVIV NO 0viV 9*EE2+08 A-6E I*t62-E6 NO UV1Y t*E92-tI NO OVIV NO QVIV NO UY1V E'912-ES 1-6E )'t02-IZ NO UVIV T*EI3-IE NO OVIV NO UVIV NO OVIV I*E62-OL 2H-69 I*8L2+09 9*002+09 t*092+OS NO UVIV 6*>I2+OS NO UY1V I*602+06 2H-61 E*0E2-0S P*T02-09 I'882-09 NO UVIV 9'ILE-09 NO QVIV ' I*EL2+00 MS-6$ E*E02+09 I*382+09 9*893+0S NO UVIV I*392+09 NO UVIV 4*LS2+06 HO-66 MO UVIV 6*6I2+0) I*862+0P NO UVIV E*E92+OS NO QVIV Z*E02+OS 13-66M P*EES-EI I*EE3-ZO I*S92-I6 NO UVIV I'892-T6 S*663-EI L*EE2-IB 13-101 0*002+00 O*002+00 0*002+00 NO UVIV O*002+00 0*002+00 0*002+00 HO-10E I*092+08 NO UV1Y )*SE2+OL NO UV1Y )*032+09 NO OVIV I*EE2+IO MA-I0S S*tES-ES NO OVIV E*It3-EG NO UY1V L*002-EL NO UVIV E*EES-ES Hn-109 E*812+06 NO UVIV E*SS2+09 NO QVIV S*tE3+06 NO OVIV I'8E2+II vc-IT0m 9*9L2+09 9*142+09 E'9L2+09 NO OVIV I*EI3+OL NO GY1V Z*SE2+06 12-IESW E*S62+09 *I*E02+08 t*8I2+04 I*082+08 I*t93+06 NO QVIV I*tE2+06 12-IELm I*IE2+06 E*662+08 I*E93+08 E'8S3+08 t*Gt2+06 NO UVIV E*LS2+06 12-IEL Z*062-10 L*SE2-II t*SE2-II I*SS3-IO 8*SE2-IO I*9S2-08 12-IE6M t*EE3+08 NO.UVIV I*IE3+06 I*L62+08 E'863+08 t*LE2+06 NO GVIV S*L02+06 12-136 0*002+00 0*002+00 0'002+00 0*002+00 O*003+00 NO UVIV 0*002+00 12-IEIM t*S02+0E E*E02+02 I'8E2+03- E*t82+0E E*EE2+0E NO QVIV Z*182+09 12-IEI 0'002+00 O*003+00 0*003+00 O*003+00 0*003+00 NO QVIV O*002+00 3qINION-T C-6D ua^*IS-L/6L i
1 l CPS-ODCM TABLE 3.5-27 (continued) MEAT PATHWAY FACTORS - R".n (ADULT) (m# mrem /yr per pCi/sec) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE TE-132 1.42E+06 9.21E+05 8.64E405 1.02E+06 8.87E+06 NO DATA 4.36E+07
~
I-130 2.03E-06 5.90E-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-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 C3-138 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 2.88E+07 3.62E+04 1.89E+06 NO DATA 1.23E+04 2.07E+04 5.94E+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+0'O IA-140 3.68E-02 1.85E-02 4.90E-13 NO DATA NO DATA NO DATA 1.36E+03 IA-142 4.07E-91 1.85E-92 4.61E-93 NO DATA NO DATA NO DATA 1.35E-8,8 CE-141 1.39E+04 9.43E+03 1.07E+03 NO DATA 4.38E+03 NO DATA 3.61E+0.7 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 0.00E+00 0.00E+00 NO DATA 0.00E+00 NO DATA 0.00E+00
*D-147 7.04E+03 8.14E+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 2.57E-01 2.53E-02 1.39E-02 NO DATA 7.88E-02 NO DATA 5.18E+03
- mrem /yr per Ci/m
**1.45 x 10-'
l I CLINTON-1 3-95 Rev.15-7/97
CPS-ODCM i TABLE 3.5-28 I VEGETATION PATHWAY FACTORS - Rh (CHILD) (m# mrem /yr per Ci/sec) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE H-3 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* NA-24 3.75E+05** 7.01E+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 CR-51 NO DATA 9.30E+07 NO DATA 1.17E+05 6.49E+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 0.02E+08 4.25E+08 1.32E+08 NO DATA NO DATA 2.40E+08 FE-59 3.98E+08 7.88E+07 6.43E+08 3.21E+08 NO DATA NO DATA 1.87E+08 6.70E+08 CO-58 NO DATA 6.44E+07 1.97E+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 HI-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 CU-64 NO DATA 1.21E+03 1.09E+04 6.59E+0'4 NO DATA 2.64E+04 NO DATA 5.12E+05 EN-G5 8.11E+08 2.16E+09 1.34E+09 NO DATA 1.36E+09 NO DATA ZN-69 3.79E+08 9.29F-06 1.34E-05 1.24E-06 NO DATA 8.14C-06 NO DATA 8.46E-04 BR-83 NO DATA NO DATA 5.40E+00 NO DATA NO DATA NO DATA NO. DATA ER-84 NO DATA NO DATA 3.92E-11 NO DATA NO DATA i NO DATA NO DATA BR-85 NO DATA NO DATA NO DATA NO DATA NO DATA RB-86 NO DATA NO DATA NO DATA 4.53E+08 2.79E+08 NO DATA NO DATA RB-88 NO DATA 2.91E+07 NO DATA 4.38E-22 3.04E-22 NO DATA NO DATA RB-89 NO DATA NO DATA 2.15E-23 4.69E-26 4.17E-26 NO DATA NO DATA NO DATA 4.09E-28
'-89 3.59E+10 NO DATA 1.03E+09 NO DATA NO DATA NO DATA i-90 1.24E+12 1.39E+09 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 Y-91m 6.58E+07 9.24E-09 NO DATA 3.36E-10 NO DATA NO DATA NO DATA 1.81E-05 Y-91 1.06E+07 NO DATA 4.97E+05 NO DATA NO DATA Y-92 i 1.58E+00 NO DATA 2.48E+09 NO DATA 4.52E-02 NO DATA NO DATA NO DATA 4.57E+04 Y-93 2.92E+02 NO DATA 8.01E+00 No DATA NO DATA ZR-95 3.86E+06 NO DATA 4.35E+06 8.49E+05 7.56E+05 NO DATA 1.22E+06 NO DATA , 8.86E+08 ER-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 MO-99 1.50E+05 NO DATA 2.95E+08 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 TC-101 5.24E+03 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 RU-105 3.86E+07 NO DATA 3.97E+08 9.16E+01 NO DATA 3.32E+01 NO DATA 8.05E+02 RU-106 7.45E+08 NO DATA 5.98E+04 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 TE-125m NO DATA 4.04E+07 NO DATA 2.58E+09 3.51E+08 9.52E+07 4.68E+07 9.86E+07 NO DATA NO DATA TE-127m 1.32E+09 3.39E+08 3.56E+08 1.57E+08 3.16E+08 3.77E+09 NO DATA 1.07E+09 TE-127 9.84E+03 2.65E+03 2.11E+03 6.81E+03 TE-129m 2.80E+04 NO DATA 3.84E+05 8.43E+08 2.35E+08 1.31E+08 2.72E+08 2.47E+09 TE-129 1.32E-03 NO ' DATA 1.03E+09 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+G6 NO DATA 2.16E+07 _TE-131 2.59E-15 7.89E-16 7.71E-16 1.98E-15 7.83E-15 NO DATA 1.36E-14 CLINTON-1 3-96 Rev.15-7/97
CPS-ODCM TABLE 3.5-20 (continued) I VEGETATION PATHWAY FACTORS - Rh (CHILD) (m# mrem /yr per pCi/sec) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE TE-132 7.00E406 3.10E+06 3.74E+06 4.51E406 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 I-131 1.43E+08 1.44E+08 8.16E+07 4.75E+10 2.36E+08 NO DATA 1.28E+07 I-132 9.20E+01 1.69E+02 7.77E+01 7.84E+03 2.59E+02 NO DATA 1.99E+02 1-133 3.53E406 4.36E+06 1.65E+06 8.11E+08 7.27E+06 NO DATA 1.76E+06 I-134 1.50E-04 2.79E-04 1.28E-04 6.41E-03 4.26E-04 NO DATA 1.85E-04 1-135 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 1.44E-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 2.40E-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 - LA-140 3.24E+03 1.13E+03 3.53E+02 NO 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 No DATA 9.22E-27 NO DATA 3.75E-23
*D-147 7.16E+04 5.80E+04 4.49E+03 NO DATA 3.18E+04 NO DATA 9.18E+07 -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 Ci/m
**3.75 x 10' CLINTON-1 _ _ _ _ _ _ _ _
3-97 Rev.15-7/97
3dS-OGDH 1VIEI'3 E
- S- 2 6 A3931V1 ION dVIHMVA g
3V31 OHS - H% )133N(
)m mlaW/AJ dOJ 1TO T (
OHDVN3 GON3 I'I A3H 1*GOGA 1HAHOIG XIGN3A I'nND D I -I'I'I IS01Od3 H-0 NO QVIV Z*G63+00 2*963+OE. 2*S63+0E* 2*G63+0E, 2*563+0E, 2*963+OE, 3-ID I*t93+09, Z*6I3+OS, Z*6I3+0S. Z*6I3+OS, 2*6I3+OS. 2*6I3+05 2*6I3+OS* NV-ED 2*t03+05,, 2*p03+OS Z*t03+OS 2*t03+OS 2*p03+OS 2*t03+OS 2*t03+OS d-EZ I'9I3+06 6*6L3+OL 9*2t3+OL NO QVIV NO QVIV NO QVIV I*ES3+00 3H-SI NO QVIV NO QVIV 9*I23+0> E't03+0> I*Cp3+OP 8*Lt3+OD I*0E3+OL HN-SP NO QVIV >*St3+00 6*013+0L NO QVIV I*E93+08 NO QVIV 6*E23+08 HN-S9 NO QVIV I*DC3+OI 2*993+00 NO QVIV 33-SS E*293+08 I*813+01 NO QVIV 6*tI3+02 2*EI3+00 9*E63+OL NO QVIV NO QVIV I*>93+08 I*003+08 33-S6 I'L63+08 )*183+08 I'9I3+00 NO QVIV NO QVIV I*E23+08 6 883+08 3C-S8 NO QVIV P*E93+OL I*OI3+08 NO QVIV NO QVIV NO QVIV 30-90 9*023+08 NO QVIV 2*>63+08 G*903+00 NO QVIV NO QVIV NO QVIV E*Z>3+06 NI-9E I'9I3+IO I*It3+06 S*t93+00 NO QVIV NI-99 NO GY1V NO QVIV I'8I3+08 G*LE3+OI L*C23+00 C*Et3+00 NO QVIV NO QVIV NO GY1V E*6L3+02 3n-9# NO QVIV 8*383+OE E*603+0E NO QVIV E*T03+09 NO QVIV 9*)33+0S 2N-9S t*EE3+08 I*t43+06 9*893+08 NO UY1V 6*tI3+08 NO QVIV 9*ZE3+08 2N-96 q*093-09 6*903-09 9*L23-OL NO QVIV 9*283-09 NO QVIV I'LL3-09 3U-8E NO QVIV NO QVIV Z*6E3+00 NO QVIV NO QVIV NO QVIV NO QVIV JU-89 NO QVIV NO QVIV 3*EI3-II NO GY1V NO QVIV NO QVIV NO QVIV GM-BG NO QVIV NO QVIV NO QVIV NO QVIV NO QVIV NO QVIV NO QVIV B8-89 NO QVIV 3*LE3+08 I*283+00 NO QVIV NO QVIV NO QVIV t*023+04 B8-88 NO QVIV E*IL3-ZZ I'963-ZZ NO QVIV NO QVIV NO QVIV Z*L23-36 38-86 NO QVIV E'993-29 2*923-29 NO QVIV NO QVIV NO QVIV S*tS3-ES
.i-86 I*SI3+IO NO QVIV t*EE3+08 NO QVIV NO QVIV NO QVIV I*003+06 7-60 L*S03+II NO QVIV I*893+II NO QVIV NO QVIV NO QVIV 3*II3+IO sH-61 2*823+09 NO QVIV I*IE3+09 NO QVIV NO QVIV NO QVIV I*283+09 SU-6E )*003+02 NO QVIV I'L03+OI NO QVIV NO GV1V NO QVIV I*0Z3+09 A-60 I*393+0P NO QVIV E*EL3+OE NO QVIV NO QVIV NO QVIV I*0E3+08 X-6IW G*093-06 NO QVIV I*6E3-IO NO QVIV NO QY1V NO QVIV Z*E83-OL A-6I L*8)3+09 NO QVIV 3*I03+09 NO QVIV NO QVIV NO QVIV E*EI3+06 A-62 8*903-01 NO QVIV 2*t62-0E NO QVIV NO QVIV NO QVIV Z*E93+OP A-6E I'983+02 NO QVIV )*Ct3+00 NO QVIV 2H-69 NO GY1V NO QVIV )*8E3+09 I*LE3+09 S*t93+OS E*LS3+OS NO QVIV 8*023+OS NO QVIV I*293+06 2E-6L E*T03+03 9*1t3+01 Z*8E3t01 NO QVIV 6*EI3+OI NO QVIV ' I'993+OL NE-69 I*623+OS I*OL3+OS G*893+0> NO QVIV I*0E3+OS HO-66 NO QVIV >*S93+08 NO QVIV S*9t3+09 I*083+09 NO QVIV I*363+OL NO QVIV I*OI3+OL 43-66m g*LE3+00 L*9I3+00 6*893+01 NO QVIV I*IE3+02 t*ZE3+00 S*003+OE 13-101 8*OZ3-EI I*It3-EO I*I23-26 NO QVIV 2*093-26 9*6S3-EI I*693-EL un-I0E 9'8I3t09 NO QVIV 3*613+09 NO QVIV Z*t03+OL NO QVIV 9*963+08 un-IOS t*6L3+01 NO GYIV I*6E3+OI NO QVIV- 9'EL3+02 NO QVIV t*013+0P un-109 E*063+08 NO QVIV E'863+OL NO QVIV G*6S3+08 NO QVIV I*t83+IO yc-ttom I*SI3+OL I*tE3+OL 8*LE3+09 NO QVIV Z*LE3+OL NO QVIV t 0E3+06 13-Iggm I*t63+08 S*ES3+OL I*663+OL t*IS3+OL NO QVIV NO QVIV )*E83+08 12-IZLm q*g23+08 I*693+08 9'9L3+OL I*EI3+08 3*Z)3+06 13-IZL S*t03+0E NO QVIV I*E83+06 I*6E3+0E I*I93+0E E*LE3+OE 3*I63+09 NO,QVIV )*IL3+09 13-IE6m E'903+08 I*EP3+08 S*L03+OL I*193+08 I*SI3+06 N0 GY1V 13-126 I*ES3+06 L*IE3-09 Z*993-09 I*LE3-ot 9*063-OD Z*663-0E NO QVIV C*603-OE 13-IEIm 8*tP3+OS >*093+OS E*E83+OS 9*063+OS >*233+09 13-IEI NO QVIV E'Z93+OL I*tI3-IS S*003-19 t*E63-I9 I*003-IS 9'IS3-IS NO QVIV I*IS3-I9 5
DI' INION-I E-68 uaA*IS-L/6L
3 CPS-ODCM TABLE 3.5-29 (continued) VEGETATION PATHWAY FACTORS - Rh (TEEN) )
- (m# mrem /yr per pCi/sec)
BRGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ' ISOTOPE WE-132 3.91E+06 2.4BE+06 2.33E+06 2.61E+06 2.37E+07 NO DATA 7.84E+07 lI-130 3.50E+05 1.01E+06 4.05E+05 8.26E+07 1.56E+06 NO DATA 7.79E+05 lI-131 7.66E+07 1.07E+08 5.76E407 3.13E+10 1.85E+08 NO DATA 2.12E+07 ,I-132 5.19E+01 1.36E+02 4.87E+01 4.58E+03 2.14E+02 NO DATA 5.91E+01 i
- I-133 1. 93E4 06 3.28E+06 1.00E+06 4.58E+08 5.75E+06 NO DATA 2.48E+06 I
'I-134 8.44E-05 2.24E-04 0.03E-05 3.73E-03 3.53E-04 NO DATA 2.95E-06 I-135 3.53E+04 9.09E+04 3.37E+04 5.85E+06 1.44E+05 NO DATA 1.01E+05 @S-134 7.10E+09 1.67E+10 7.75E+09 NO DATA 5.31E+09 2.03E+09 2.08E+08 @S-136 4.37E+07 1.72E408 1.16E+08 NO DATA 9.37E+07 1.48E+07 1.38E+07 5S-137 1.01E+10 1.35E+10 4.70E+09 NO DATA 4.59E+09 1.78E+09 1.92E+08 @S-138 3.54E-11 6.80E-11 3.40E-11 NO DATA 5.02E-11 5.84E-12 3.08E-14 BA-139 2.70E-02 1.90E-05 7.86E-04 NO DATA 1.79E-05 1. 31 E-05 2.41E-01 l BA-140 1.38E+08 1.69E+05 8.89E+06 NO DATA 5.73E+04 1.14E+05 2.13E+08 I BA-141 1.11E-21 8.27E-25 3.70E-23 NO DATA 7.67E-25 5.66E-25 2.36E-27 i BA-142 5.35E-39 5.35E-42 3.29E-40 NO DATA 4.53E-42 3.56E-42 1.64E-50 LA-140 1.80E+03 8.86E+02 2.36E+02 NO DATA NO DATA NO DATA 5.09E+07 IA-142 1.88E-04 8.35E-05 2.00E-05 NO DATA NO DATA NO DATA 2.54Et00 l @E-141 2.83E+05 1.89E+05 2.17E+04 NO DATA 8.90E+04 NO DATA 5.41E+08 I CE-143 9.33E+02 6.79E+05 7.58E+01 NO DATA 3.04E+02 NO DATA 2.04E+07 l CE-144 5.29E+07 2.19E+07 2.84E+06 NO DATA 1.31E+07 NO DATA 1.33E+10 ! GR-143 7.00E+04 2.79E+04 3.48E+03 NO DATA 1.62E+04 NO DATA 2.30E+08 I PR-144 3.04E-26 1.24E-26 1.54E-27 NO DATA 7.14E-27 No DATA 3.35E-29
'D-147 3.62E+04 3.94E+04 2.36E+03 NO DATA 2.31E+04 NO DATA 1.42E+08 *187 3.53E+04 2.88E+04 1.01E+04 NO DATA NO DATA NO DATA 7.79E+06 UJP-239 1.39E+03 1.31E+02 7.26E+01 NO DATA 4.10E+02 NO DATA 2.10E+07 9mrs:m/yr per 5
Ci/m 3 C*2.40 x 10 I
^
l l l t i LINTON-1 3-99 Rev.15-7/97
CPS-ODCM TABLE 3.5-30 VEGETATION PATHWAY FACTORS - Rh (ADULT) (m# mrem /yr per pCi/sec) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LL[ ISOTOPE H-3 NO DATA 2.26E+03* 2.26E+03* C-14 2.26E+03* 2.26E+03* 2.26E+03* 2 . 2 6 E+ 03
- 8.97E+05* 1.79E405* 1.79E+05* 1.79E405* 1.79E+05*
NA-24 2.71E+05** 1.79E+05* 1.79E+05* 2.71E405 2.71E+05 2.71E+05 2.71E+05 2.71E+05 P-32 1.40E409 8.70E+07 5.41E+07 2.71E+05 NO DATA NO DATA NO DATA 1.57E+08
~
CR-51 NO DATA NO DATA 4.60E+04 2.75E+04 MN-54 1.01E+04 6.11E+04 1.16E+07 NO DATA 3.13E+08 5.96E+07 NO DATA 9.30E+07 MN-56 NO DATA 9.58E+08 NO DATA 1.59E+01 2.02E+00 NO DATA 2.01E+01 FE-55 2.10E+08 NO DATA 5.06E+02
~
1.45E+08 3.3BE+07 NO DATA NO DATA 8.10E+07 FE-59 1.26E+08 2.96E+08 1.13E+08 8.33E+07 NO DATA NO DATA 8.27E+07 9.86E+08 CO-58 NO DATA 3.00E+07 6.90E+07 NO DATA NO DATA NO DATA CO-60 NO DATA 1.67E+08 3.69E+08 6.24E+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 CU-64 NO DATA 9.16E+03 4.30E+03 2.04E+02 NO DATA 2.31E+04 NO DATA ZN-65 3.18E+08 1.01E+09 4.57E+08 7.81E+05 NO DATA 6.76E+08 NO DATA 6.36E+08 ZN-69 5.39E-06 1.03E-05 7.17E-07 CR-83 NO DATA NO DATA 6.69E-06 NO DATA 1.55E-06 NO DATA 3.13E400 NO DATA NO DATA BR-84 NO DATA NO DATA 4.50E+00 NO DATA 2.54E-11 NO DATA NO DATA LR-85 NO DATA 1.99E-16 NO DATA NO DATA NO DATA NO DATA RB-86 NO DATA NO DATA NO DATA NO DATA 2.19E+08 1.02E+08 NO DATA RB-88 NO DATA No DATA 4.33E+07 NO DATA 3.43E-22 1.82E-22 NO DATA RB-89 NO DATA NO DATA 4.74E-33 NO DATA 3.96E-26 2.79E-26 NO DATA 89 NO DATA NO DATA 2.30E-39
'j.-90 9.95E+09 NO DATA 2.86E+08 NO DATA NO DATA 6.04E+11 NO DATA 1.60E+09 NO DATA 1.48E+11 NO DATA NO DATA SR-91 NO DATA 1.75E+10 3.02E+05 NO DATA 1.22E+04 NO DATA NO DATA SR-92 4.28E+02 NO DATA 1.44E+06 NO DATA 1.85E+01 NO DATA NO DATA Y-90 1.33E+04 NO DATA 8.48E+03 NO DATA 3.56E+02 NO DATA NO DATA Y-91m NO DATA 1.41E+08 5.42E-09 NO DATA 2.10E-10 NO DATA NO DATA Y-91 5.12E+06 NO DATA 1.37E+05 NO DATA 1.59E-08 Y-92 NO DATA NO DATA NO DATA 2.82E+09 9.13E-01 NO DATA 2.67E-02 NO DATA NO DATA Y-93 1.69E+02 NO DATA 1.60E+04 NO DATA 4.65E+00 NO DATA NO DATA ZR-95 1.18E+06 NO DATA 5.35E+06 3.79E+05 2.56E+05 NO DATA 5.94E+05 ER-97 3.36E+02 6.78E+01 No DATA , 1.20E+09 3.10E+01 NO DATA 1.02E+02 NO DATA NS-95 1.42E+05 7.91E+04 2.10E+07 4.25E+04 NO DATA 7.82E+04 NO DATA HO-99 NO DATA 6.12E+06 1.16E+06 4.80E+08 TC-99m NO DATA 1.39E+07 NO DATA 1.42E+07 3.09E+00 8.73E+00 1.11E+02 NO DATA TC-101 1.33E+02 4.28E+00 5.16E+03 8.62E-31 1.24E-30 1.22E-29 NO DATA 2.24E-29 RU-103 4.77E+06 NO DATA 6.35E-31 3.73E-42 2.06E+06 NO DATA 1.82E+07 NO DATA RU-105 5.36E+01 NO DATA 2.12E+01 5.57E+08 NO DATA 6.93E+02 NO DATA 3.28E+04' RU-106 1.93E+08 NO DATA 2.44E+07 AG-110m NO DATA 3.73E+08 NO DATA 1.25E+10 1.05E+07 9.75E+06 5.79E+06 NO DATA TE-125m 9.67E+07 1.92E+07 NO DATA 3.98E+09 3.51E+07 1.30E+07 2.91E+07 3.93E+08 TE-127m 3.49E+08 NO DATA 3.86E+08 1.25E+08 4.26E+07 8.93E+07 1.42E+09 TE-127 5.65E+03 2.03E+03 NO DATA 1.17E+09 1.22E+03 4.19E+03 2.30E+04 NO DATA TE-129m 2.51E+08 9.35E+07 3.97E+07 4.46E+05 TE-129 8.61E+07 1.05E+09 NO' DATA 1.26E+09 l 7.61E-04 2.86E-04 1.85E-04 5.84E-04 l
TE-131m 9.12E+05 3.20E-03 NO DATA 5.75E-04 4.46E+05 3.72E+05 7.06E+05 4.52E+06 TE-131 1.51E-15 6.32E-16 4.78E-16 NO DATA 4.43E+07 1.24E-15 6.63E-15 NO DATA 2.14E-16 l CLINTON-1 3-100 Rev.15-7/97
3 CPS-ODCM i TABLE 3.5-30 (continued) ~ VEGETATION PATHWAY FACTORS - Rh (ADULT) (m' mrem /yr per Ci/sec) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE f TE-132 4.31E+06 2.79E+06 2.62E+06 3.08E+06 2.68E+07 NO DATA 1.32E+08 I-130 3.91E405 1.15E+06 4.55E+05 9.77E+07 1.80E+06 NO DATA I-131 8.07E407 1.15E+08 9.93E+05 6.62E407 3.78E+10 1.98E+08 NO DATA 3.05E+07 I-132 5.77E+01 1.54E+02 5.40E+01 5.40E+03 2.46E+02 NO DATA 1-133 2.09Et06 3.63E+06 2.90E+01 1.11E+06 5.34E+08 6.34E+06 NO DATA 3.26E+06 I-134 9.33E-05 2.53E-04 9.06E-05 4.39E-03 4.03E-04 NO DATA 2.12E-07 I-135 3.91E+04 1.02E+05 3.77E+04 6.75E+06 1.64E+05 NO DATA CS-134 4.67E+09 1.11E+10 1.16E+05 l 9.08E+09 NO DATA 3.59E+09 1.19E+09 1.94E+08 CS-136 4.26E+07 1.68E+08 1.21F.408 NO DATA CS-137 9.35E+07 1.28E+07 1.91E+07 6.36E+09 8.70E+09 5.70E+09 NO DATA 2.95E+09 9.82E408 CS-138 3.84E-11 1.68E+08 7.58E-11 3.75E-11 NO DATA 5.57E-11 5.50E-12 3.23E-16 l BA-139 2.86E-02 2.04E-05 8.38E-04 BA-140 NO DATA 1.91E-05 1.16E-05 5.07E-02 1.29E+08 1.62E+05 8.43E+06 NO DATA 5.50E+04 9.26E+04 BA-141 1.18E-21 0.90E-25 2.65E+08 3.98E-23 NO DATA 8.28E-25 5.05E-25 5.55E-31 BA-142 5.79E-39 5.96E-42 3.64E-40 l NO DATA 5.03E-42 3.37E-42 LA-140 1.98E+03 8.16E-57 { 9.95E+02 2.63E+02 NO DATA NO DATA NO DATA LA-142 2.04E-04 9.25E-05 7.31E+07 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 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 NO DATA PR-143 8.14E+06 NO DATA 1.11E+10 6.26E+04 2.51E+04 3.10E+03 NO DATA 1.45E+04 NO DATA PR-144 2.74E+08 3.25E-26 1.35E-26 1.65E-27 NO DATA 7.61E-27 NO DATA l
'D-147 4.68E-33 1 3.33E+04 3.85E+04 2.31E+03 NO DATA 2.25E+04 NO DATA -187 3.80E+04 1.85E+08 3.18E+04 1.11E+04 NO DATA NO DATA NO DATA 1.40E+07 HP-239 1.43E+03 1.40E+02 7.74E+01 NO DATA 4.38E+02 NO DATA 2.88E+07
- mrem /yr per5 pCi/m'
- 2.71 x 10
. I 1
1 @LINTON-1 3-101 Rev.15-7/97
C PS-ODCM l i TABLE 3.5-33 GROUND PLANE PA'IHWAY FACTORS - R$ (m# mrem /yr per Ci/sec) TOTAL TOTAL TOTAL ISOTOPE BODY SKIN ISOTOPE BODY SKIN ISOTOPE BODY SKIN H-3 0.00E+00 0.00E+00 Y-91 1.07E406 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 4.10E+05 P-32 0.00E+00 0.00E+00 ZR-95 2.45E+08 2.85E408 EA-139 1.06E+05 1.19E405-CR-51 4.65E+06 5.50E+06 ZR-97 2.96E+06 3.44E+06 BA-140 2.05E+07 2.35E+07 MN-54 1.38E+09 1.62E409 ND-95 1.37E+08 1.61E+08 BA-141 4.17E+04 4.75E+04 MN-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 CO-58 3.80E+0B 4.45E+08 RU-103 1.08E+08 1.26E+08 CE-141 1.37E+07 1.54E+07 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 NI-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 1.84E+03 ZN-65 2.11E+03 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 2R-83 2.73E+06 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 LR-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 4.99E+06 RB-89 1.23E+05 1.48E+05 I-130 5.50E+06 6.68E+06
'-89 2.16E+04 2.50E+04 I-131 1.72E+07 2.09E+07 .-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 S R'-92 7.77E+05 8.64E+05 I-134 4.46E+05 5.30E+05 Y-90 4.50E+03 5.31E+03 I-135 2.53E+06 2.95E+06 Y-91m 1.00E+05 1.16E+05 CS-134 6.07E+09 8.01E+09 *1.20 x 10 l
l ? l i f CLINTON-1 3-102 Rev.15 7/97
CPS-ODCM 4.0 COMPLI ANCE WITil 40CFR190 4.1 Total Dose - Operation and Surveillance Requirements OPERATION REQUIREMENT The annual (calendar year) dose or dose commitment to any MEMBER OF THE PUBLIC due to releases of radioactivity and to radiation from uranium fuel cycle sources shall be limited to less than or equal to 25 mrem to the total ! body or any organ, except the thyroid, which shall be ! limited to less than or equal to 75 mrem. This requirement is applicable at all times. REMEDIAL REQUIREMENT:
- a. With the calculated doses from the release of radioactive materials in liquid or gaseous effluents '
exceeding twice the limits of Sections 2.4.l(a), 2.4.l(b), 3.5.l(a), 3. 5.1 (b) , 3. 5.2 (a) , and 3.5.2(b), calculations shall be made including i direct radiation contributions from the reactor unit ' and from outside storage tanks to determine whether the above limits of Section 4.1 have been exceeded. If such is the case, prepare 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 10CFR20 Part 2203(4), shall i include the following information: l
- 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 facilitics located beyond the 5-mile radius from CPS need not be considered in this determination.
- 2. A determination of the maximum exposed individual.
CLINTON-1 4-1 Rev.15-7/97
CPS-ODCM
- 3. A determination of the total annual dose to the
- maximum exposed individual from all existing pathways and sources of radioactivity and l radiation (including direct radiation from N-l 16, the plant and storage facilities) using methodologies described in this manual. The l direct radiation dose may be either calculated
! using NUREG-0133 methodology or measured.# l 4. It shall describe the levels of radiation and concentrations of radioactive material l involved, and the cause of the exposure levels i or concentrations. ! If the estimated dose (s) exceeds the above limits, and if the release condition resulting in violation of 40CFR Part 190 has~not already been corrected, the Special Report shall include a request for a variance in accordance with the provisions of 40CFR Part 190. i Submittal of the report is considered a timely l request, and a variance is granted until staff J action on the request is complete. l SURVEILLANCE REQUIREMENTS
- 4.1.1 Cumulative dose contributions from liquid and gaseous i
effluents shall be determined in accordance with Sections l 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 manual. 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).
#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 4-2 Rev.15 7/97
CPS-ODCM 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM The primary requirements for the Clinton Power Station Radiological Environmental Monitoring Program (REMP) are set forth in Table 5.1-1 and shown by location in Figures 5.0-1, 5.0-2, 5.0-3 and 5.0-4. I l In addition to the required sampling program, CPS will perform supplemental periodic and long term sampling and analyses in order to better monitor 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 by collecting aliquots of fixed volume at fixed time intervals. This method of sampling is considered consistent with note (g) in Table 5.1-1. 5.1 Monitoring Program - Operation and Surveillance Requirements OPERATION REQUIREMENT The Radiological Environmental Monitoring Program shall be conducted as specified in Table 5.1-1. This requirement applies at all times. REMEDIAL REQUIREMENT:
- 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 5.6.2, a description of the reasons for not conducting the program as required and the plans for preventing a recurrence.
l I l CLINTON-1 5-1 Rev.15-7/97
CPS-ODCM
- 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 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 to be taken to reduce radioactive effluents to that the potential annual dose to a MEMBER OF THE PUBLIC is 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 submitted if:
concentration (1) + concentration (2) + >1.0 reporting level (1) reporting level (2) When radionuclides other than those in Table 5.1-2 are detected and the result of plant effluents, this report shall 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 effluents; however, in such an event, the condition shall be reported and described in the Annual Radiological Environmental Operating Report.
- c. With milk or fresh leafy vegetation samples unavailable from one or more of the sample locations required by Table 5.1-1, identify locations for obtaining replacement samples and add them to the radiological environmental monitoring program within 30 days. The specific locations from which samples were unavailable may then be deleted from the monitoring program. Pursuant to Technical Specification 5.6.2, identify the cause of the
~The methodology and parameters used to estimate the potential annual dose to a MEMBER OF THE PUBLIC shall be indicated in this report.
CLINTON-1 5-2 Rev.15-7/97
CPS-ODCM unavailability of samples and identify the new location (s) for obtaining replacement samples in the. next annua 1' Radiological Environmental Operating 'd I Report and also include in the report a revised figure (s) and table for this manual reflecting the new location (s). SURVEILLANCE REQUIREMENTS l 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, arxi 5.0-4 and shall be analyzed pursuant to the requirements of Table 5.1-1 and the detection-capabilities required by Table 5.1-3. i l l l I II i CLINTON-1 5-3 Rev.15-7/97 2
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l CPS-ODCM TABLE 5.1-1 (Continued) RADIOLOGICAL ENVIRONMENTAL HONITORING PROGRAM l TABLE NOTATIOVS l
- Refer to NUREG-0133, " Preparation of Radiological Effluent Technical Specifications for Nuclear Power Plants," October 1978, and to Radiological Assessment Branch Technical Position, Revision 1, November 1979. Deviations are permitted from the required sampling schedule if specimens are unobtainable due to hazardous conditions, seasonal unavailability, malfunction of automatic sampling equipment and other legitimate reasons. If specimens are unobtainable due to sampling equipment malfunction, every effort shall be made to complete corrective action prior to the end of the next sampling period. All deviations from the sampling schedule shall be documented in the Annual Radiological Environmental Operating Report pursuant to Technical Specification 5.6.2. It is recognized that, at times, it may not be possible or practicable to continue to obtain samples of the media of choice at the most desired location or time.
In these instances suitable alternative media and locations may be chosen for the particular pathway in questios and appropriate substitutions made within 30 days in the radiological environmental monitoring program. Technical Specification 5.6.2, identify the causePursuant of the to unavailability of samples for that pathway and identify the new location (s) for obtaining replacement samples in the next annual Radiological Environmental Operating Report and also include in the report a revised figure (s) and table for the ODCM reflecting f*('. the new location (s) .
'One or more instruments, such as a pressurized ion chamber, for measuring and recording dose rate continuously may be used in place of, or in addition to, integrating dosimeters. For the purposes of this table, a thermoluminescent dosimeter (TLD) is considered to be one phosphor; two or more phosphors in a packet are considered as two or more dosimeters. Film badges'shall not be used as dosimeters for measuring direct radiation. The 40 stations is not an absolute number. The number of direct radiation monitoring stations may be reduced according to geographical limitations; e.g., at an ocean site, 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 l information with minimal fading. , CLINTON-1 5-14 l Rev.15-7/97
i C PS -ODCM TABLE 5.1-1 (Continued) RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM TABLE NOTATIONS (Continued) f 'The purpose of this sample is to obtain background information. If it is not practical to establish control locations in accordance with the distance and wind direction criteria, other sites that provide valid background data may be substituted. d l Airborne particulate sample filters shall be analyzed for gross l beta radioactivity 24 hours or more after sampling to allow for i 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.
' Gamma isotopic analysis means the identification and quantification of gamma-emitting radionuclides that may be attributable to the effluents from the facility. )
l
'The " upstream sample" shall be taken at a distance beyond significant influence of the discharge. The " downstream" sample shall be taken in an area beyond but near the mixing zone. " Upstream" samples in an estuary must be taken far enough upstream to be beyond the plant influence. Salt water shall be sampled only when the receiving water is utilized for recreational activities. 'A composite sample is one in which the quantity (aliquot) of liquid sampled is proportional to the quantity of flowing liquid (or time) and in which the method of sampling employed results in l a specimen that is representative of the liquid flow. In this j program composite sample aliquots shall be collected atstime i i intervals that are very short (e.g., hourly) relative to the l
compositing period (e.g., monthly) in order to assure obtaining a representative sample.
" Groundwater samples shall be taken when this source is tapped for drinking or irrigation purposes in areas where the hydraulic l
gradient or recharge properties are suitable for contamination.
*The dose shall be calculated for the maximum organ and age group, using the methodology and parameters in Section 2.4.2.
( CLINTON-1 5-15 Rev.15-7/97
1 h Cps-oDCM TABLE 5.1-1 (Continued) RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM TABLE NOTATIONS (Continued) 8 1f harvest occurs more than once a year, sampling shall be performed during each discrete harvest. If harvest occurs continuously, sampling shall be monthly. Attention shall be paid to including samples of tuberous and root food products.
"The dose shall be calculated for the maximum organ and age group, using the methodology and parameters in Section 3.5.4.
1 CLINTON-1 5-16 Rev.15-7/97
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CPS-ODCM TABLE 5.1-3 (Continued) DETECTION FOR ENVIRONMENTAL SAMPLE ANALYSIS TABLE NOTATIONS
'This list does not mean that only these nuclides are to be considered. Other peaks are identifiable, together with those of.
the above nuclides, shall also be analyzed and reported in the Annual Radiological Environmental Operating Report pursuant to I Technical Specification 5.6.2.
' Required detection capabilities for thermoluminescent dosimeters )
used for environmental measurements shall be in accordance with the recommendations of Regulatory Guide 4.13, Rev. 1, July 1977.
*The 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 dstected with 95% probability with only 5% probability of falsely concluding that a blank observation represents a "real" signal.
For a particular measurement system, which may include radiochemical separation: LLD = 4. 66sb/ [E
- V
- 2.22
- Y ~ exp (-lat) ]
Where: LLD is the "a priori' lower limit of detection as defined above, as picocuries per unit mass or volume, l 1 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, - l E if the counting efficiency, as counts per disintegration, V is the sample size in units of mass or volume, I 2.22 is the number of disintegrations per minute per picocurie, 1 I Y is the fractional radiochemical yield, when applicable, A is the radioactive decay constant for the particular I radionuclide (sec") , and ] l CLINTCN-1 5-19 Rev.15-7/97 )
CPS-ODCM ot for environmental samples is the elapsed time between sample collection, or end of the sample collection period, and time of counting (sec). l 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 posteriori (after the fact) limit for a particular measurement. Analyses shall be performed in such a manner that the stated LLct 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 unachievcble. In such cases, the contributing factors shall be identified and described in the Annual Radiological Environmental Operating Report pursuant to Technical Specification 5.6.2.
+
CLINTON-1 5-20 Rev.15-7/97 .
CPS-ODCM 5.2 Land Use Census - Operation and Surveillance Requirements OPERATION REQUIREMENT A land use census shall be conducted and shall identify within a distance of 8 km (5 miles) the location in each of the 16 meteorological sectors of the nearest milk animal, the nearest residence and the nearest garden
- of greater than 50 m2 (500 ft2) producing broad leaf vegetation. For evaluated or mixed-mode releases as defined in Regulatory Guide 1.111, Revision 1, July 1977, the land use census shall also identify within a distance of 5 km (3 miles) the location in each of the 16 meteorological sectors of all milk animals and all gardens of greater than 50 m2 producing broad leaf vegetation. This requirement applies at all times.
REMEDIAL REQUIREMENT:
- 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 new location (s) in the next annual Radiological Environmental Operating l 86 ,( Report, pursuant to Technical Specification 5.6.2. 3 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 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
- 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 sect 6rs with the highest predicted D/Qs in lieu of the garden census. Specifications for broad leaf vegetation sampling in Table 5.1-1.4c shall be followed, including analysis of control samples. CLINTON-1 5-21 Rev.15-7/97
CPS-ODCM I pathway, may be deleted from this monitoring program after October 31 of the year in which this land use census was conducced. Pursuant to Technical Specification 5.6.3, identify the new location (s) in the next Radioactive Effluent Release Report and also include in the report a revised figure (s) and table for this manual reflecting the new location (s) . SURVEILLANCE REQUIREMENTS 5.2.1 The land use census shall be conducted during the growing season at least once per 12 months using that information that will provide the best results, such as by a door-to-door survey, aerial survey, or by consulting local agriculture authorities. The results of the land use census shall be included in the annual Radiological Environmental Operating Report pursuant to Technical Specification 5.6.2. 5.3 Interlaboratory Comparison Program l All analyses for CPS Radiological Environmental Monitoring Program are performed by Teledyne Isotopes Midwest Laboratories (TIML) located in Northbrook, Illinois. Teledyne Isotopes Midwest Laboratory has participated in interlaboratory comparison (cross-check) programs since l 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. I analytical precedures and to alert it to any possible problems. l Participant laboratories measure the concentrations of l 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 specific ranges indicate a need to check the instruments or procedures used. CLINTON-1 5-22 Rev.15-7/97
I 1 CPS-ODCM If the results of a determination in the EPA cross-check , 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 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 i Interlaboratory Comparison Program are prescribed in Section 5.3.1 (which follows). 5.3.1 Interlaboratory Comparison Program - Operation and Surveillance Requirements OPERATION REQUIREMENT Analyses shall be performed on all radioactive materials, supplied as part of an Interlaboratory Comparison Program ' l that has been approved by the Commission, that correspond to samples required by Table 5.1-1. This requirement applies at all times. REMEDIAL REQUIREMENT:
- a. With analyses not being performed as required above, t
report the corrective actions taken to prevent a rec.urrence to the Commission in the Annual Radiological Environmental Operating Report pursuant to Technical Specification 5.6.2. SURVEILLANCE REQUIREMENTS 5.3.1.1 The Interlaboratory Comparison Program is described in Section 5.3. A summary of the results obtained.as part of the above required Interlaboratory Comparison Program shall be included in the Annual Radiological Environmental Operating Report pursuant to Technical Specification 5.6.2. l l l CLINTON-1 5-23 Rev.15-7/97
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i w CLINTON-1 5-27 Rev.15-7/97
CPS-ODCM 6.0 BASES FOR OPERATION AND SURVEILLANCE REQUIREMENTS 6.1 General Operation and Surveillance Requirements 1 ! 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 necessary to constitute compliance with the terms of an individual Operation Requirement and associated REMEDIAL REQUIREMENT. 1.3.1 This requirement provides that surveillance activities, necessary to ensure the Operation Requirements are met, will be performed during the conditions for which the Operation Requirements are applicable. Some surveillance activities may be requi' red 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 tolerances for performing surveillance activities beyond those specified in the nominal surveillance interval. These tolerances 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 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. l l t CLINTON-1 6-1 Rev.15-7/97 l
CPS-ODCM 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 l are assumed to be OPERABLE if the associated surveillance ! activities have been satisfactorily performed within the i specified time interval. Nothing in this provision is to be construed as defining equipment, systems or components I OPERABLE, when such items are found or known to be inoperable although still meeting the Surveillance Requirements. 1.3.4 This requirement ensures that surveillance activities associated with a Operatio'n 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 surveillance activities must be performed within the stated surveillance interval prior to placing or returning the system or equipment into OPERABLE status. 6.2 Monitoring Instrumentation l Section 2.7: Radioactive Liquid Effluent Monitoring Instrumentation The radioactive liquid effluent instrumentation is provided to monitor and control, as applicable,-the l releases of radioactive materials in liquid effluents during actual or potential releases of liquid effluents. The alarm / trip setpoints for these instruments shall be calculated and adjusted in accordance with the methodology and parameters in this manual to ensure that the alarm / trip wil.1 occur prior to exceeding the limits of 10CFR 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 l 10CFR Part 50. I ? CLINTON-1 6-2 Rev.15-7/97
CPS-ODCM Section 3.9.1: Offgas Radiation Monitoring l Instrumentation l l The OPERABILITY of the radiation monitoring ! instrumentation ensures that; (1) the radiation levels l 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 10CFR Part 50, Appendix A, General Design Criteria 19, 60, 61, 63 an. o4. Section 3.9.2: Radioactive Gaseous Effluent Monitoring Instrumentation The radioactive gaseous effluent instrumentation is 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 pararneters in this manual to ensure that the alarm / trip will occur prior to exceeding the limits of 10CFR 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 10CFR Part 50. The sensitivity of any noble gas activity monitors used to show compliance with the gaseous effluent release requirements of Section 3.5.1 shall be such that concentrations as low as 1 x 10" pCi/ml are measurable. 6.3 Radioactive Effluents - 6.3.1 Liquid Effluents Section 2.3.1: Liquid Effluent Concentration This requirement is provided to ensure that the concentration of radioactive materials released in liquid waste effluents to UNRESTRICTED AREAS will be less than the concentration levels specified in 10CFR Part 20, Appendix B, Table 2, Column 2. This limitation provides additional assurance that the levels of radioactive materials in bodies of water in UNRESTRICTED AREAS will result in exposures within (1) the Section II.A design objectives of Appendix I, 10CFR Part 50, to a MEMBER OF CLINTON-1 6-3 Rev.15-7/97 .
CPS-ODCM i I THE PUBLIC and (2) the limits of 10CFR Part 20.3301 to l i 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 lim in air (submersion) was converted to an equivaler.t concentration in water using the methods described in International Commission on Radiological Protection (ICRP) Publication
- 2. ,
l This requirement applies to the release of radioactive materials in liquid effluents from the site. The required detection capabilities for radioactive I 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 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 2.4.1: 10CFR50, Appendix I Release Rate Limits This requirement is provided to implement the requirements of Sections II.A, III.A and IV.A of Appendix I, 10CFR 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 set forth in Section IV.A of Appendix I to assure that the releases of radioactive material in liquid effluents to UNRESTRICTED AREAS will be kept "as low as , is reasonably achievable." Also, for fresh water sites with drinking water supplies that can be potentially affected by plant operations, there is reasonable assurance that the operation of the facility will not result in radionuclide concentrations in the finished drinking water that are in excess of-the requirements of 40CFR 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 based on models and data, such that the. actual exposure of a MEMBER OF THE PUBLIC through appropriate pathways is unlikely to be substantially underestimated. The equations specified in this manual for calculating the i doses due to the actual release rates of radioactive materials in liquid effluents are consistent with the l CLINTON-1 6-4 Rev.15-7/97
l ces-oocM j methodology provided in Regulatory Guide 1.109,
" Calculation of Annual Doses to Man from Routine Releases l of Reactor Effluents for the Purpose of Evaluating Compliance with 10CFR Part 50, Appendix I," Revision 1, October 1977 and Regulator y Guide 1.113, " Estimating Aquatic Dispersion of Effl1ents from Accidental and Routine Reactor Releases fo" the Purpose of Implementing Appendix I," April 1977.
This requirement applies to the release of radioactive materials in liquid effluents from the one reactor unit on the site. Section 2.5.1: Liquid 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 of radioactive materials in liquid effluents will be kept-
"as low as is reasonably achievable." This specification implements the requirements of 10CFR Part 50.36a, General Design Criterion 60 of Appendix A to 10CFR Part 50 and the design objective given in Section II.D of appendix I to 10CFR Part 50. The specified limits governing the use of appropriate portions of the liquid radwaste treatment l system were specified as a suitable fraction of the dose design objectives set forth in Section II.A of Appendix I, 10CFR Part 50, for liquid effluents.
This requirement applies to the release of radioactive materials in liquid effluents from the one reactor unit l on the site. - l 6.3.2 Gaseous Effluents Section 3.4.1: 10CFR20 Release Rate Limits This requirement is provided to ensure that the dose at any time at and beyond the SITE BOUNDARY from gaseous effluents from all units on the site will be within the annual dose limits of 10CFR Part 20 to UNRESTRICTED AREAS. The annual dose limits are the doses associated with the concentrations of 10CFR Part 20, Appendix B, Table 2, Column 1. These limits provide reasonable assurance that radioactive material discharged in gaseous effluents will not result in the exposure of a MEMBER OF CLINTON-1 6-5 Rev.15-7/97
CPS-ODCM THE PUBLIC in an UNRESTRICTED AREA, either within or outside the SITE BOUNDARY, to annual average concentrations exceeding the limits specified in Appendix B, Table 2 of 10CFR Part 20. For MEMBERS OF THE PUBLIC who may at times be within the SITE BOUNDARY, the occupancy of that MEMBEF OF THE Pv8LIC will usually be sufficiently low to conpensate for any increase in the atmospheric diffusion factor above that for the SITE BOUNDARY. Examples of such MEMBERS OF THE PUBLIC, with the appropriate occupancy factors, shall be given in this manual. Doses for such MEMBERS OF THE PUBLIC are provided in the Radioactive Effluent Release Report. The specified release rate limits restrict, at all times, the corresponding 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 mrem / 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 dose 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 materials in gaseous waste samples are tabulated in terms of the lower limits of detection (LLDs). Detailed discussion of the LLD, and other detection limits can be found in 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 3.5.1: Noble Gas Dose This requirement is provided to implement the requirements of Sections II.B, III.A and IV.A of Appendix I, 10CFR Part 50. The 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 forth in Section IV.A of Appendix I to assure that the releases of radioactive material i.n gaseous effluents to UNRESTRICTED ARFAS will be kept "as low as is reasonably achievable." The Surveillance Requirements implement the requirements in Section III. A of Appendix I CLINTON-1 6-6 Rev.15-7/97
\
CPS-ODCM l that conformance with the guides of Appendix I be shown i by calculational procedures ' cased on models and data such l that the actual exposure of a MEMBER OF THE PUBLIC through appropriate pathways is unlikely to be substantially underestimated. The dose calculation i methodology and parameters established in this manual for l calculating the doses due to the actual release rates for l radioactive noble gases in gaseous effluents are consistent with the methodology provided in Regulatory Guide 1.109, " Calculation of Annual Doses to Man from Routine Releases of Reactor Effluents for the Purpose of Evaluating Compliance with 10CFR Part 50, Appendix I," Revision 1, October 1977 and Regulatory Guide 1.111, i
" Methods for Estimating Atmospheric Transport and Dispersio'n of Gaseous Effluents in Routine Releases from
! Light-Water Cooled Reactors" Revision 1, July 1977. The equations in this manual for determining the air doses at and beyond 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: Iodine-131, Iodine-133, Tritium, and Radionuclides in Particulate Form This requirement is provided to implement the requirements of Sections II.C, III.A and IV.A of Appendix I, 10CFR 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 material 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 Ann.ual Doses to Man from Routine Releases of Reactor Effluents for the Purpose of Evaluating Compliance with 10CFR Part 50, Appendix I," Revision 1, October 1977 and Regulatory CLINTON-1 6-7 Rev.15-7/97
CPS-ODCM Guide 1.111, " Methods for Estimating Atmospheric Transport and Dispersion of Gaseous Effluents in Routine Releases from Light-Water Cooled Reactors" Revision 1, July 1977. These equations also provide for determining the actual doses based upon the real time atmospheric conditions. The release rate specifications for iodine-131, tritium, and radionuclides in particulate form with half lives greater than 8 days are dependent upon the existing radionuclide pathways to man in the areas at and beyond the SITE BOUNDARY. The pathways that were examined in the development of these calculations were: (1) individual inhalation of airborne radionuclides, (2) deposition of radionuclides onto green leafy vegetation with subsequent consumption by man, (3) deposition onto grassy areas where milk animals and meat producing animals graze with con.sumption of the milk and meat by man, and (4) depositiore on the ground with subsequent exposure of man. This requirement applies to the release of radioactive materials in gaseous effluents from one reactor unit on the site. Sections 3.6 and 3.7: Gaseous Radwaste (Offgas) Treatment and Ventilation Exhaust Treatment System l l 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, i l provides reasonable assurance that the releases of ; radioactive mater ~ials in gaseous effluents will be kept J "as low as reasonably achievable." This requirement implements the requirements of 10CFR Part 50.36a, General Design Criterion 60 of Appendix A to 10CFR Part 50 and the design objectives given in Section II.D of Appendix I to 10CFR 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, 10CFR Part 50, for gaseous effluents. This requirement applies to the release of radioactive materials in gaseous effluents from the one' reactor unit on the site. - CLINTON-1 6-8 Rev.15-7/97
CPS-ODCM 6.3.3 Total Dose Section 4.1: Total Dose l { This requirement is provided to meet the dose limitations of.40CFR Part 190 that have been incorporated into 10CFR 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 effluents and direct radiation exceed 25 mrem to the total body or-any organ, except the thyroid, which shall be limited ~to less than or equal to 75 mrem. For sites containing up to 4 reactors, it is highly unlikely that the resultant dose to a MEMBER OF THE'PUBLIC will exceed the dose limits of 40CFR Part 190 if the individual reactors remain within twice the dose design. objectives of Appendix I, and if direct radiation doses from the reactor units and.outside storage tanks are kept small. The Special Report will describe a course.of action that should result in the limitation of the annual dose to a MEMBER OF THE PUBLIC-to within the 40CFR Part 190 limits. For the purposes of the Special Report, it may be assumed that the dose commitment to the MEMBER OF THE PUBLIC from other uranium fuel 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 40CFR Part 190, the Special Report with a request for a variance (provided the release conditions resulting in violation of 40CFR Part 190 have not already been corrected), in accordance with the provisions of 40CFR Part 190.11 and 10CFR Part 20.2203, is considered to be a timely request and fulfills the requirements of 40CFR Part 190 until NRC staff action is completed. The variance only relates to the limits of 40CFR Part 190, and does not apply in any way to the other requirements for dose limitation of 10CFR Part 20, as addressed in Sections 2.3 and 3.4. An individual is not considered a i 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. CLINTON-1 6-9 Rev.15-7/97 i
CPS -ODCM 6.4 Radiological Environmental Monitoring Section 5.1: Monitoring Program The radiological environmental monitoring program required by this requirement provides representative measurements of radiation anc of radioactive materials in those exposure pathways and for those radionuclides that lead to the highest potential radiation exposures of MEMBERS OF THE PUBLIC resulting from the station operation. This monitoring program implements Section IV.B.2 of Appendix I to 10CFR 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 Radiological Assessment Branch Technical Position on Environmental Monitoring, Revision 1, November 1979. The initially specified monitoring j program will be effective for at least the first.three- l years of commercial operation. Following this period, l 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 c;e considered optimum for routine environmental measurements in industrial laboratories. It should be recognized that the LLD is defined as an a priori (before the fact) limit representing the capability of a. i measurement system and not as an a posteriori (after the fact) limit for a particular measurement. - Detailed discussion of the LLD, and other detection limits, can be found in currie, L. A., " Lower Limit of Detection: Definition and Elaboration of a Proposed , Position for Radiological Effluent and Environmental Measurements," NUREG/CR-4007 (September 1984), and in the HASL Procedures Manual, HASL-300 (revised annually). Section 5.2: Land Use Census This requirement 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 CLINTON-1 6-10 Rev.15-7/97
CPS-ODCM 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, questionnaire, or from consulting with local agricultural authorities). This census satisfies the requirements of Section IV.B.3 of Appendix I to 10CFR Part 50. Restricting the census
, to gardens of greater than 50 m* provides assurance that significant exposure pathways via leafy vegetables will be identified and monitored since a garden of this size is the minimum required to produce the quantity (26 kg/ year) of leafy vegetables assumed in Regulatory Guide 1.109 for consumption by a child. To determine this minimum garden size, the following assumptions were made:
(1) 20% of the garden was used for growing broad leaf vegetation (i.e., similar to lettuce and cabbage) and (2) a vegetation yield of 2 kg/m*. Section 5.3.1: Interlaboratory Comparison Program The requirement for participation in an approved Interlaboratory Comparison Program is provided to ensure that independent checks on the precision and accuracy of the measurements of radioactive 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 10CFR Part 50. l CLINTON-1 6-11 Rev.15-7/97
i CPS-ODCM 7.0 REPORTING REQUIREMENTS 7.1 Annual Radiological Environmental Operating Report I Routine Radiological Environmental Operating Reports I covering the operation of the unit during the previous l calendar year shall be submitted prior to May 1 of each l year pursuant to Technical Specification 5.6.2. The Annual Radiological Environmental Operating Reports shall include the following information:
- 1. Summaries, interpretations, and an analysis of l trends of the results of the radiological l environmental surveillance activities for the report i
period, including a comparison with preoperational studies, with operational controls as appropriate, , and with previous environmental surveillance l 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 l and tabulated results of these analyses and l 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.
~One map shall cover stations near the site boundary and a second f map shall include the more distant stations.
1 CLINTON-1 7-1 Rev.15-7/97
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- 6. The results of licensee participation in the f Interlaboratory Comparison Program, required by Section 5.3.1.
- 7. Discussion of all deviations from the sampling schedule of Table 5.1-1.
- 8. Discussion of all analysis in which the LLD required by Table 5.1-3 was not achievable.
7.2 Radioactive Effluent Release Report
. Routine Radioactive. Effluent Release Reports covering the operation.of the unit during the previous 12 months of operation shall be submitted by May 1 of each year pursuant to Technical Specification 5.6.3.
The Radioactive Effluent Release Report shall include the following information:
- 1. A summary'of the quanti, ties of radioactive liquid and gaseous effluents and solid waste released from 1 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 10CFR 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 defined by 10CFR 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,whether determined by measurement or estimate),
CLINTON-1 7-2 Rev.15-7/97
i i ! CPS-ODCM L ! d. Source of waste and processing employed (e.g., l dewatered spent resin, compacted dry waste, evaporator bottoms). l
- 3. A list and description of unplanned releases from' the site to UNRESTRICTED AREAS of radioactive
- materials in gaseous and liquid effluents made during the reporting period.
l l 4. A listing of new locations for dose calculations and/or environmental monitoring identified by the land use census pursuant to Section 5.2. l S. Changes to the ODCM pursuant to Technical l Specification 5.5.1. l
- 6. Major changes to radioactive , liquid, gaseous, and l
solid waste treatment systems . The discussion of each change shall contain:"
- a. A summary of the evaluation that led to the l determination that the change could be made in I accordance with 10CFR Part 50.59.
- b. Sufficient detailed information to totally support the reason for the change without benefit of additional or supplemental information; i
l c. A detailed description of the equipment, ! components and processes involved and the j interfaces with other plant systems;
- d. An evaluation of the change, which shows the l 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;
*EIcensees may choose to submit the information called for in ,t,his requirement as part of its annual USAR update.
Changes described by this requirement shall become effective upon review by the FRG. 1 CLINTON-1 7-3 Rev.15-7/97
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- 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
- 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 ac'ceptable by the FRG.
The Radioactive Effluent Release Report shall also include the following information:
- 1. An annual summary of hourly meteorological data collected over the previous year. This annual summary may be either in the form of an hour-by-hour listing on magnetic tape of wind speed, wind direction, atmospheric stability, and precipitation (if measured), or in the form of joint frequency distributions of wind speed, wind direction, and atmospheric stability.
- 2. An assessment of the radiation doses due to the radioactive liquid and gaseous effluents released i
from the unit or station 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. Annual average meteorological { conditions or meteorological conditions concurrent with the time of release of radioactive material's in gaseous effluents, as determined by sampling frequency and measurements, may be used for determining the gaseous CLINTON-1 7-4 Rev.15-7/97
I l CPS-ODCM
- pathway doses. The assessment of radiation doses shall be performed in accordance with the methodology and parameters in this manual. I
- 4. An assessment of radiation doses to the likely most 4 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 40CFR Part 190, Environmental l Radiation Protection Standards for Nuclear Power ' Operation. Acceptable methods for calculating the dose contribution from liquid and gaseous effluents are given in Regulatory I Guide 1.109, Rev. 1, October 1977. , lI l l l i l l l l l CLINTON-1 7-5 Rev.15-7/97
CPS-ODCM 8.0 ADJUSTMENT OF THE CPS ODCM METHODOLOGY Consistent with the NRC Commissioners' opinion on 10CFR50 Appendix I dated April 30, 1975, CPS will use environmental 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 using environmental monitoring data, uncertainties associated with plume behavior, radiciodine chemical form, deposition and retention of forages, and milk consumption patterns may be circumvented or reduced. l l l l l i J CLINTON-1 8-1 Rev.15-7/97
1 i CPS-ODCM 9.0 ATMOSPilERIC TRANSPORT AND DISPERSION MODEL L 9.1 Introduction The atmospheric transport and dispersion model used by Illinois Power Company is a straight-line, sector-l 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.I.c l " Constant Mean Wind Direction Models". All meteorological and dose calculations prescribed in this manual are based on meteorological data concurrent with the time of release or the annual average values. l Near-real time meteorological data processing is prescribed in Section 9.2. 9.2 Concurrent Meteorological Data Processing Meteorological data is acquired and processed through a model which utilises bi-level hourly meteorological ~ f 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 are generated for each dose l receptor location as follows: 1 Relative undecayed, undepleted plume concentration (X/Q) Relative decayed and depleted radioiodine and particulate concentration (D2DPXQ) Relative decayed noble gas concentration (DlXQ) 1 I
- Relative particulate and radiciodine deposition (D/Q) l Standard deviations of the undecayed, undepleted j plume concentrations CLINTON-1 9-1 Rev.15-7/97
CPS-ODCM Since the Regulatory Guide 1.111 depletion and deposition curves are defined only within the range encompassing 100 to 200,000 meters, analysis results are not considered valid outside this range. The following sections describe the calculations performed by the transport and dispersion model for a one hour time interval. 9.2.1 Determination of Pasquill 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: AT = (Tu - T t) / (Hu - Ht ) , *C/ meter (1) where Tu = Meteorological (twet) tower upper level temperature, *C Tt= Meteorological tower lower level temperature, C Hu = Meteorological tower upper level instrumentation l height ! = 60 meters ) l l He= = Meteorological tower level instrumentation height l 10 meters AT is then classified according to the following scheme: Pasquill Stability Defining Cond'i tion l A (Extremely Unstable) -0.900 < AT < -0.019 B -0.019 < AT < -0.017 l C -0.017 < AT < -0.015 1 D (Neutral) -0.015 < AT < -0.005 E F
-0.005 < AT 5 0.015 0.015 < AT < 0.040 G (Extremely Stable) 0.040 < AT < 0.900 Invalid AT $ -0.900 or AT > 0.900 CLINTON-1 9-2 Rev.15-7/97
CPS-ODCM 9.2.2 Calculation of Stack Height Wind Speed The wind speed at the release point (HVAC Exhaust Stack or Standby Gas Treatment System Exhaust Stack) height, STACWS, is calculated using the expressions: STACWS = WSPu (STACKH/Hu) ", meter /sec (2) P= [ log (WSPt /WSPu) ] / [ log (Ho/Hu) ) , dimensionless (3) where WSPu = Upper met tower level wind speed, meter /sec WSP t = 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 Release Mode and the Entrainment Coefficient The mode of release can be elevated, ground or mixed; the latter being a combination of the first two. The 4 mode of release, as well as an entrainment coefficient, TCORR, are determined from the stack height, STACH, building height, BLDGHT, stack exit velocity, EXITV, and wind speed at the stack height, STACWS. For effluents exhausted from release points that are higher than twice the height of adjacent solid structures, . 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 points or vents at the level of, or above, odjacent solid structures, but lower than elevated release points, CLINTON-1 9-3 Rev.15-7/97
CPS-ODCM 2 (BLDGHT) > STACKH > BLDGHT (6) the release is treated as elevated, ground or mixed according to the following relationships: ELEVATED: TCORR = 0.00 if EXITV >S(STACWS) (7) GROUND: TCORR = 1.0 if EXITV < STACWS (8) MIXED: TCORR = 0.30-0.06(EXITV/STACWS) if (9) 5(STACWS) 2 EXITV > 1.5 (STACWS) TCORR = 2.58-1.58(EXITV/STACWS) if (10) 1.5(STACWS) 2 EXITV > (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 then evaluated separately and the concentration X/Q calculated according to the fraction of the time each release occurs. 9.2.4 Calculation of Vertical Standard Deviation The vertical plume spread (vertical standard deviation), r, is a function of the distance from the
) release point to the reception point for a given Pasquill stability class. The numerical value of r, if obtained by a polynominal fitting equation which simulates Figure 1 of Regulatory Guide 1.111:
r2 = 10[A + B log (X) +C (log (X) ) *] , meter (11) where . { X = Distance to a specific receptor, kilometer A,B,C = Empirical factors which vary by stability I class, determined by fitting polynominal equations to the Regulatory Guide 1.111 Figure 1 curves, dimensionless i CLINTON-1 9-4 Rev.15-7/97
C PS-ODCM Empirical Factors Used in Equation (11) Pasquill Class A B C A 2.79166 2.69043 1.07483 8 2.11394 1.47930 0.40676 C 1.81954 0.88317 -0.06101 l 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 be specified which limits the value of r, to be no greater than this value. 9.2.5 Calculation of the Building Wake Correction For ground-based and mixed-mode releases, an adjustment is made in the calculation of X/O 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 vertica'l plume spread equation (11): Z,= [a,* + 0.5 (BLDGHT)#/x] (12) with the requirement that E' is restricted to values E, < ( 3 ) b (or) . 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 of the exhausted effluent, AH, is calculated. For Pasquill stability classes A,B,C and D, AH is calculated per section 9.2. 6.1; for classes E,F and G, section 9.2.6.2 is used. , 9.2.6.1 AH For Pasquill Class A,B,C and D AH is calculated using both equations (13) and (14) and the minimum value is selected for use. In addition, when the vertical exit velocity, EXITV, is less than 1.5 times the horizontal windspeed, STACWS, a downwash correction is subtracted from equation (13) per equation (15). , CLINTON-1 9-5 Rev.15-7/97
CPS-ODCM AH = 1. 4 4 (STACD) (EXITV/STACWS)"' (13) ( X/ STACD) "'-DOWNWASH, meter AH 2 = 3. 0 (STACD) (EXITV/STACWS) , meter (14) DOWNWASH = 3. 0 (STACU) (1. 5-EXITV/STACWS) , meter (15) where STACD = Internal release point stack diameter
= 3.77 meters (HVAC Exhaust Stack)
= 0.44 meters (SGTS Exhaust Stack)
EXITV = Stack exit velocity, meter /second-X = Distance to specified receptor, meter lrd-All other parameters are as defined previously. 9 '. 2 . 6 . 2 AH For Pasquill Class E, F and G AH is determined by selecting the minimum value calculated by equations (13) and (14) above and equations (16) and (17) below: AH 3 = 4. 0 [ (0. 5 (EXITV) (STACD) ) */S] , meter (16) AH 4 =
- 1. 5 [ (O. 5 (EXITV) (STACD) ) 2/STACWS] l (S) ~1,
meter (17) where S= Restoring acceleration per unit vertical displacement for adiabatic motion, sec~*'
=
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 Height 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) CLINTON-1 9-6 Rev.15-7/97
j' 1
)
1 CPS-ODCM where TERAIN = Difference between the plant base height above mean sea level (MSL) and the receptor point height above MSL, meter _>0.0. j 9.2.8 Determination of Affected Sectors 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* 2 WD < 360.00* 2 NNE 11.25* 2 WD 2 33.75* 3 NE 33.75* 2 WD < 56.25* 4 ENE 56.25* 2 WD < 78.75* 5 E 78.75* 2 WD < 101.25* 6 ESE 101.25* 2 WD < 123.75* 7 SE 123.75* 2 WD < 146.25' . 8 SSE 146.25* 2 WD < 168.75* l 9 S 168.75* 2 WD < 191.25* 10 SSW 191.25* 2 WD < 213.75* 11 SW 213.75* 2 WD < 236.25'
) 12 WSW 236.25* 2 WD < 258.75* !
13 W 258.75* 2 WD < 281.25' i 14 WNW 281.25* 2 WD < 303.75* l 15 NW 303.75* 2 WD < 326.25* 16 NNW 326.25* 3 WD < 348.75* l 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 same at both levels, the resulting X/O will be summed into the same sector; otherwise, the X/O 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. CLINTON-1 9-7 Rev.15-7/97
CPS-ODCM 9.2.9 Calculation of Depletion 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 polynominal equations developed to simulate the Regulatory Guide curves. Both the DPF and DPSP calculations depend on the effective plume height, H, the stability class, S, and the distance, X, to the receptor. l The Regulatory Guide 1.111 curves represent plumes that l 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 meters 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 topography does change with 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 curve 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 Height (meters) J Value O f H $ 15 5 15 < H $ 45 6 45 < H $ 80 7 H > 80 8 Similarly, the stability class is categorized into one of three S-ranges as fellows: l CLINTON-1 9-8 Rev.15-7/97
l ; l CPS-ODCM { l Stability Class S. Value i A, B, C 1 D 2 l E, F, G 3 l 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 i Value X (meters) A DPF l gt, d l 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 > 60,000 A = 25 calculated 24 all X 1.0 DPF is calculated using the value for A and equations (19) and (20) :
DPF = B(A) + B (A + 1 ) d + B ( A + 2 ) d* + B ( A + 3 ) d' (19) d = log (X) (20) 1 l CLINTON-1 9-9 Rev.15-7/97
CPS-ODCM The corresponding values for the B(A), B(A + 1), B(A 4
- 2) and B(A + 3) terms are as follows:
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 (meters) C DPSF l @' g 5 X < 100 0 X > 100 C=1 calculated 6 X E 100 0 X > 100' C=8 calculated
- 7 X < 100 0 X > 100 C = 29 calculated 8 X E 100 0 X > 100 C = 50 calculated 10 all X 0 12 X < 100 0 X > 100 C = 15 calculated 14 X E 120 0 X > 120 C = 36 calculated 15 all X 0 16 X < 210 0 X > 210 C = 57 calcul'ted a
18 X E 2900 0 X > 2900 C = 22 calculated CLINTON-1 9-10 Rev.15-7/97
I 1 CPS-ODCM 21 X< 26,000 0 I X > 26,000 C = 43 calculated l 24 all X 0 I i i DPSP is calculated using the value for C and equations I l (20), (21), and (22): ? DPSF = 10'/ (0. 392699X) (21) Y = A(C) + A (C+ 1) d + A (C+2) d" + A (C+ 3) d' (22)
+ A (C+ 4 ) d' + A) (C+ 5) d' + A (C+ 6) d' l
The corresponding values for the A(C), A(C+1), A (C+2 ) , A (C+3) , A(C+4), A(C+5) and A(C+6) terms are as follows: A(1) = -3.17821 A(33) = 7.552876 A(2) = .153463 A(34) =
.82569984 A(3) = .0759066 A(35) =
.036134823 A(4) = 0. A(36) =
-~53.7335 l A(5) = 0. A(37) =
45.3671 A(6) = 0. A(38) =
-15.3282 A(7) = 0. A(39) =
2.24735 l A(8) = -25.7331 A(40) =
.122674 I A(9) = 26.2738 A(41) = 0.
A (10) = -11.3014 A(42) = 0. i A(11) = 2.04278 A(43) =
-674.351 A (12) = .134412 A(44) = 384.531 A (13) = 0. A(45) = -73.7766 A (14 ) = 0. A(46) = 4.72041 A(15) = -47.5827 A(47) = 0.
l A(16) = 43.8050 A(48) = 0. l A (17) = -16.0781 A(49) = 0. A (18) = 2.53726 A(50) = -55.5622 A(19) = .148044 A(51) = 53.6534 A(20) = 0. A(52) = -20.6300 A(21) = 0. A(53) = 3.44177 A(22) = -128.5278 A(54) = .212314 A(23) = 77.28943 A(55) = 0. l A(24) = -15.90284 A(56) = 0. l A(25) = 1.071885 A(57) = S36.987302 l A(26) = 0. A(58) = -755.860224 l A(27) = 0. A(59) = 515.64145 A(28) = 0. A(60) = -181.713295 A(29) = 41.824767 A(61) = 35.153579 A(30) = -103.969677 A(62) = -3.558356 A (31) = 86.215344 A(63) = .14774 I A(32) =
-35.1021096 I i
I I 1 CLINTON-1 9-11 Rev.15-7/97
CPS-ODCM 3 9.2.10 Ground Level X/0, D2DPXQ, D1XQ, D/O Analysis 9.2.10.1 Undecayed, Undepleted Plume Relative Concentration, X/Q The atmospheric concentration of effluent at ground level, normalized by the source term Q, is given by the following equation: X/Q = 2.032 (TCORR) /WSPt (;X ) Amin, sec/m' (23) where l l A in = The lesser of the two values obtained by equations (24) and (25), meter A1 = (c", + E ,) , meter (24) A2 = (3) c z , Meter (25) b 2.032 = The constant (2/x) divided by the width in radians'of a 22.5* sector (i.e., x/8, dimensionless X = Distance between release point to receptor, meter
~i 9.2.10.2 Decayed, Depleted Radiciodine and Particulate Relative Concentration, D2DPXQ The decayed, depleted radiciodine concentration, D2DPXQ, is calculated in accordance with the following equation:
D2DPXQ = DPF(DC2)X/Q, sec/m 3 (26) where DPF = The depletion factor calculated per section 9.2.9, dimensionless DC2 = The radioiodine decay factor, dimensionless
= exp[-0.693(X)/ty(WSP t)]
= exp[-0.693 (X) / (8 day) (24 hr/ day) (3600 sec/hr) (WSPt )]
CLINTON-1 9-12 Rev.15-7/97
CPS-ODCM
=
exp [-1. 00E-0 6 (X /WS P i ,) ] I 9.2.10.3 Decayed Noble Gas Plume Relative Concentration, D1XQ _ The decayed noble gas plume relative concentration, D1XQ, is calculated in accordance with the following equation: D1XQ = DC1 (X /0) , sec/m' (27) where DC1 = The noble gas decay factor, dimensionless
= exp [-0.693 (X) /ty(WSP t) ]
= exp [-0. 693 (X) / (2.26 day) (24 hr/ day)
(3600 sec/hr) (WSPo))
= exp [-3.55E-06 (X/WSPt )]
9.2.10.4 Radiciodine and Particulate Relative Deposition, D/Q ! i The relative deposition for radioiodines and l' particulates, D/Q is calculated in accordance with the following equation: l t D/Q = [DPSF(DC2) (TCORR) ] / [ (2n/16)X] , m* - (28) where i DPS F = The deposition factor calculated per section
- 9. 2 . 9, m*
9.2.11 Elevated X/Q, D2DPXQ, D1XQ, D/O Analysis 9.2.11.1 Undecayed, Undepleted Plume Relative Concentration, X/Q The atmospheric concentration of effluent at elevated lM'd level, normalized by the source term Q, is given by the following equation: 1 X/Q = [2. 03} (1-TCORR) exp [-0. 5 (H/cz) 2] ] / [STACWS (X) c z], sec/m (29) , where all parameters are as previously defined. l l l l CLINTON-1 9-13 l L Rev.15-7/97
CPS-ODCM { 9.2.11.2 Decayed, Depleted Radiciodine and Particulate Relative Concentration, D2DPXQ The calculation of D2DPXQ for elevated releases follows section 9.2.10.2 methodology with the exception that the WSPt value used in the calculation of DC2 in equation (26) is replaced by the STACWS value and the equation (29) X/O is used. 9.2.11.3 Decayed Noble Gas Plume Relative Concentration, D1XQ The calculation of D1XQ for elevated releases follows section 9.2.10.3 methodology by substituting the equation (29) X/O value into equation (27) and STACWS for WSPt in the calculation of DC1. 9.2.11.4 Radiciodine and Particulate Relative Deposition, D/O The calculation of D/O for elevated releases follows section 9.2.10.4 methodology by substituting (1-TCORR) for the TCORR term in equation (28) and STACWS for WSP t in the calculation of DC2. CLINTON-1 9-14 Rev.15-7/97
?
CPS-ODCM Table 9.2-1 GASEOUS EFFLUENT RELEASE POINT CHARACTERISTICS
= =c=u=. = = sic ,uo /
ROOF EL 8767 suCHaE SHOP RRUWC ROOF EL 7817 ,
= 170T ; 206'0' CONTROL ROOM -
t- SQTSVENT AR HANDUNG
\ UNrts W CONTAINMENT CONC.EL 0177 00 - -
! - ,. ROOF E 8477 e]~ p i I r NN nn I 00GNMENT l m em l[
/ A00F EL7907 OLP.)
f , ~ g/ Ql/Q mm 200FEL8007 / _ _ _ _ _ _ , _ _ _
,/
l R00f,EL 7887 (LP.) A, l
$_555555b,q';'
< ossacEx.ne m e - ,,mo,. !
ff s (At EL7107) )
-- L _ __ _ t/ l i
l HVAC Exhaust SGTS Exhaust Stack Stack Release Point Height (m) 61 61 Building Height (m) 58 58 I Release Point Geometry Duct Pipe Release Point Area (m") 11.15 0.15 Release Point Diameter (m) 3.77* 0.44 Annual Average Flow Rate (m'/sec) 111.71 1.89 Vertical Exit Velocity (m/sec) 10.02 12.49 OEffective 2(A/x)hdiameter CLINTON-1 9-15 Rev.15-7/97
I CLINTONPOWER STATION OFFSITE DOSE CALCULATIONMANUAL REVISION 16 l Issued: DECEMBER 13,1997 I b
l
.h CPS No. 1005.06F001_
SAFETY EVALUATION SCREENING FORM q (8.2.2.a) DOCUMENT EVALUATED: Offsita_Dosa CalculationRanual,Jievision_ k (8.2.2.b) DESCRIPTION OF CHANGE: W~ ! f R3 vised Table 3.9.2 2. Added item 3 for Inservice Calibrations on Station HVAC Exhaust and Standby Gas TrIatment System Exhaust PRMs. Added annual channel calibration requirement and new applicability Table Notations "c" and "d". I Added new Table Notations explanations c" and "d" for Table 3.9.2-2. (e.2.2.c) AFFECTED SYSTEM (S) / COMPONENT (S) / FUNCTIONS : None 10CRF50.59 APPL 1*. ABILITY DETERMINATION ( 8. 2 . 2 .1) (Refer to Appendix A for guidance for the following questions) yg3 _ yo 1 Is this a change to the facility as described in the SAR? (That is, is the design, function, or method of performing the function of a structure, system or ccxqponent described by text or drawing in the SAR being changed?) ygg L No _ Is this a change to a procedure as described in the SAR? (That is, is a procedure that is outlined, summarized or that is coapletely described in the BAR being changed?) Y33 - No 1 Is this a test or experiment not described in the SAR? (That is, is a test or experiment being conducted which might affect safe operation of the plant which was not anticipated in the BART) Ys2 - No f Does this change require a change to the CPS Tech Specs? If yes, process the change in accordance with CPS No. 1038.01. ORM Zapact (8.2.2.2) (Refer to Appa"M O B for guidance for the following question) Ya3 _ No 1 Is.this a change (other than an editorial change) to the Operational Requirements Manual? If yes, complete a safety evaluation and process the change in accordance with CPS No. 1038.03. IMPACT ON OTHER LICENSING BASIS DOCUMENTS (8.2.2.3) * (Refer to Appendix B for guidance for the following question) Yac.,4 No _ Does this change directly affect any of the following programs: Technical Specification Bases Physical Security Plan Emergency Plan QA Program Description Licensed Operacor Requalification Program Offsite Dose Calculation Manual
- i
&\L Process Control Program Fire Protection Plan Enviramental Protection Plan Rev. No. 3. Page No. 2 of 3 J
CPS No. 1005.06F001 DOCUMENT EVALUATED: OffsitiLDose_CalculationManual._Havisiong S Y-/7- $ V JUSTIFICATION FOR "YES/NO" ANSWERS: l (8.2.2.1.2, 8.2.2.3) ] Justification: This change implements Regulatory Guide 1.21, Section C.5 requirements for calibrating continuous monitors using comparisons against analysis of specific radionuclides. Analytical measurements are made to quantify specific radionuclides in continuous releases by analysis of grab samples at scheduled frequencies. The comparison is the basis for calibrating continuous monitors to establish relationships between monitor readings and concentrations of release rates of radionuclides in continuous effluent releases. An annual inservice calibration is specified in the revision. Table Notation "c" and "d" add the applicable conditions for the comparison. The, purpose of the Offsite Dose Calculation Manual (ODCM) is to provide the methodologies and parameters used for assuring compliance with the radiological effluent dose limitations provided by 10CFR20,10CFR50 Appendix A,10CFR50 Appendix 1, and 40CFR190. The ODCM contains information necessary to calculate offsite doses resulting from radioactive liquid and gaseous effluents, calculations for gaseo'us and liquid effluent monitoring alarm and trip setpoints, and the elements needed to conduct the radiological environmental monitoring program. The radioactive effluent controls program and the radiological environmental monitoring program are described.
REFERENCES:
( 8 . 2 . 2 .1. 2 ) .. Offsite Dose Calculation Manual (ODCM): Table 3.9.2-2, Table 3.9.2-2 Table Notations USAR Section: 1.8, Table 11.5-1, Table 15.2.4-3a ' Technical Specifications: 5.5.1,5.5.4 Operation Requirements Manual (ORM): 6.8.1 Regulatory Guides: 1.21 Code of Federal Regulations (CFR): 10'CFR20.1302,10 CFR 20, Appendix B, Table 2, Column 2, 10CFR50.36a,10CFR50, Appendix 1,40 CFR190, . Prepared by: Iony_innat b Dates / /[1Y/k~) / /N (8.2.3) Printed Name signature Reviewed by: p, ,$,3ff [g h W ' Date: /2'/*i7 (8.2.4) Printed Name Signature Rev. No . ._3._ Page No. 3 of 3 _ . )
CLASS CODE: SNNN1 o CPS No.1005.06F003 l '(Rev. 0) LOG - REV. Page 1 of 1_ SAFETY EVALUATION CONTINUATION SHEET Document Evaluated: Offalta Dosa Cahdatlan ManuaLBavisionX /b Wh/'[-N l Provide the justificationheferences/ explanation for all answers on cover she as follows (attach J additional sheets, as necessary): Justification (continued): Tha changes incorporated by this revision to the ODCM do not modify calculations for dose or alarm setpoints. The changes incorporated by this revision align the ODCM with Regulatory Guide 1.21-r quirements. These changes are consistent with the requirements of 10CFR20,10CFR60 Appendix A, 10CFR60 Appendix I, and 40CFR190. Calculations for dose and alarm setpoints are not modified by these chinges. This revision to the ODCM does not affect structures, systems or components. The changes being
' incorporated by this revision are administrative in nature. These changes will ensure that dose from j
radioactive effluents is monitored and reported in accordance with the requirements of Technical ' l Specifications,10CFR20,10CFR60, and 40CFR190. Since the design, function, or method of performing
, the function ot ISC is not changed by this revision, this is not a change to the facility as described in the SAR.
-{ The ODCM implements the requirements of Technical Specifications,10CFR20,10CFR60, and 40CFR einee ODCM activities are included by reference and description in the Technical Spe fications4his revision !
is considered a change to procedures as described in the SARfbecaubt, Oe.dOCMis in et Salt.. 1 P:rforming radioactive effluent surveillances and dose calculations are routine parts of the overall effluent monitoring program. The ODCM incorporates the programs and procedures necescary to ensure that . g survilliances are performed when required and that their completion is adequately documented. This change does not affect the operation of plant equipment or the ability to monitor radioactive effluents and their associated dose, therefore this revision does not constitute a test or experiment not described in the SAR. , l
=> Because these changes effect only monitoring and surveillance activities associated with the ODCM, there ,)
era no changes needed to Technical Specifications, Tech Spec Bsses, or the ORM. The ODCM changes are not contrary to Technical Specifications, Tech Spec Bases, ORM, Environmental Pl:n, Security Plan, Emergency Plan, QA Program Description, Seismic Qualification, l.icensed Operator J Requilification Program, Radiological Controls, Process Control Program, Accident Analysis, or Fire Protection Program. No changes are required to these programs as a result of the ODCM program revision. l l l
l l i CPS NO. 1005.06FOO2 l SAFETY EVALUATION FORM i (8.3.1.1.a) LOG -__92__- 226 REV. O l (8.3.1.1.b) DOCUMENT EVALUATED: Offalta Dama t i, nimeinn unnumi font ul REVISION: /h TITLE: OffsitiLDose_ Calculation _ Manual _(OOCMLChange Y./'Kys i (8.3.1.1.c) f (8.3.1.1.d) DESCRIPTION AND IMPACT OF CHANGE ON LICENSING DOCUMENTS: 1 This revision to the ODCM revised Table 3.9.2-2 and Table 3.9.2-2 Table Notations. Item 3 was added to the tCble for Inservice Calibrations on Station HVAC Exhaust and Standby Gas Treatment System Exhaust PRMs. An annual channel calibration requirement and new applicability Table Notations "c" and "d" were added. The changes implement Regulatory Guide 1.21, Section C.6 requirements for calibrating continuous monitors using comparisons against analysis of specific radionuclides. The changes do not change the intent of the ODCM and are consistent with the regulatory requirements of 10CFR20.1302,10CFR50.36a,10CFR60 Appendix 1,40CFR190, and Technical Specifications. These changes' maintain the levels of radioactive effluent control required by these regulations and do not adversely impact the reliability of effluent, dose, or setpoint calculations. , l (8.3.1.1.d)
REFERENCES:
Offsite Dos'e Calculation Manual (ODCM): Table 3.9.2-2, Table 3.9.2-2 Table Notations USAR Sections: 1.8, Table 11.6-1, Table 15.2.4-3a Technical Specifications: 5.6.1, 6.5.4 l Operation Requirements Manual (ORM): 6.8.1 Regulatory Guide: 1.21 Code of Federal Regulations (CFR): 10CFR20.1302,10 CFR20, Appendix B, Table 2, Column 2, 1 10CFR50.36a,10CFR50 Appendix 1,40CFR190 (8.3.1.1.h) Prepared by: Lo we.s C D.te, II/25/97 Name Signature l (8.3.2.2) Reviewed by: A 5d &n Ov8 9"*DM
- D ee, m't 3 '
gth . ( 8 . 3'. 3 ) Approved by: $ 1 iv .N Wm Dates l 3, %
@h lNAQ{ure:
(8.3.4) FRG: f4 Date:I E Name
'V ~ Uigdtuk Rev. No. 1
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1 i CPS NO. 1005.06F002 Page 2 of _4 _ (8.3.1.1.a) LOG ,__9 7__ - 22 6 REV. J_ DOCUMENT EVALUATED: Offsite naam calentatinn Manual (ODCMI REVISION: [ TITLE: Offalta Dnem cnienlatinn k'anuallODCMI Change f-[7-f UNREVIEWED SAFETY QUESTION DETERMINATION (8.3.1.1.e) (Attach justification for following questions on CPS.No. 1005.06F003) Part I -- Impact on equipment malfunctions evaluated as the design bases Yao No d 1. Will change increase the probability of a malfunction of equipment important to safety evaluated previously in the SAR? Yao No g 2. Will change increase the consequences of a malfunction of I equipment important to safety evaluated previously in the SAR7 Pcrt II -- Impact on accidents evaluated as the design bases Ya3 No d 3. Will change increase the probability of an accident previously evaluated in the SAR? Ya3 No 1 4. Will change increase the consequences of an accident previously evaluated in the SAR? i Part III -- Potential for creating a new type of accident or equipment malfunction Ysa No d 5. Will change create the possibility of an gccident of a different ; type than any evaluated previously in the SAR? l Yza No 1 6. Will change create the possibility of a malfunction of equipment inqportant to safety of a different type than previously evaluated in the SAR? i P rt IV -- Impact on the Margin of Safety Yss No d 7. Will change reduce the Margin of safetp as defined in the basis for any technical specification? -
SUMMARY
(8.3.1.1.f, 8.3.1.1.g) I Change is safe, no USQ exists, and requires no change to technical specifications. The change may be implemented upon FRG review. Change is safe, however there is an USQ, or requires a change to technical specifications. The change requires NRC approval prior to implementation. Rsv. No. 1
CLASS CODE: SNNNI CPS NO.1005.06F003 (Rev. 0) LOG _SL _226_ REV._o_. Page of __3_ 4_ SAFETY EVALUATION CONTINUATION SHEET Document Evaluated: offsita_ Dona calculationRanual foncu Provide the justification / references / explanation for all answers on cover sheet as follows (attach additional sheets, as necessary): Justification: Part 1: The changes incorporated by this revision to the ODCM are not pertinent to malfunctions of equipment important to safety which were evaluated as the design basis. The changes incorporated by this revision do not relate to operation of plant equipment, only to surveillance and monitoring of radioactive effluents and calculations of dose to the public. No safety-related or special scope equipment are effected by these changes. The probability of.a malfunction of equipment important to safety and an increase in the consequences of a malfunction (specifically dose to unrestricted areas) are not applicable to these ODCM changes. Part II: The Clinton Power Station OFFSITE DOSE CALCULATION MANUAL (CPS-ODCM) provides the methodologies and parameters used by lilinois Power Company (IP) to assure compliance with the radioactive effluent dose limitations stated in 10CFR20,10CFR50 Appendix A (General Design Criteria 60 and 64),10CFR60 Appendix 1,40CFR190.
- The CPS-ODCM was prepared based on guidance provided in NUREG-0133, PREPARATION OF RADIOLOGICAL EFFLUENT TECHNICAL SPECIFICATIONS FOR NUCLEAR POWER PLANTS ( Octob 1978), and NUREG-0473, RADIOLOGICAL EFFLUENT TECHNICAL SPECIFICATIONS FOR BOILING WATER REACTORS (Draft 7, to Revision 3). This manual along with station procedures'are used by CPS personnel to demonstrate compliance with the above referonood Federal Regulations.
Based on a review of the SAR, there are no evalua'ted accidents associated with radioactive effluent monitor comparisons. The ODCM is not used to operate equipment necessary to mitigate socidents. The ODCM provides calculations and methodologies to determine the extent of dose to unrestricted areas as a result of plant operations. Since the ODCM does not affect accidents previously evaluated in the SAR, these changes will not increase the probability of these evaluated accidents. . The consequences of accidents evaluated in the SAR are associated with dose to unrestricted areas as a result of radioactive effluents. This revision will improve dose determinations from radioactive gaseous effluents by ensuring the PRMs are calibrated with grab samples. The ODCM provides the monitoring and calculations requirements'to assess and report dose to unrestricted areas and the general public. Since the ODCM is used to determine the dosa related to radioactive effluents from both normal plant operation and during accidentpostulated accidents, the ODCM in itself is not capable of increasing accident consequences. ,
CLASS CODE: SNNNI CPS NO.1005. 06F003 (Rev. 0) LOG _9 7 - _226. REV. __o_ Page 4_ of _ 4 _ SAFETY EVALUATION CONTINUATION SHEET Document Evaluated: Offalta_ Dose _CalculatloaManuauODCM) Provide the justification / references / explanation for all answers on cover sheet as follows (attach tdditional sheets, as necessary): Justification (continued): PIrt lil: There are no credible accidents or equipment important to safety failure modes associated with these changes to the ODCM. The changes incorporated by this revision are being made to ensure that inservice calibrations on Station HVAC and Standby Gas Treatment System exhaust PRMs are performed annually to comply with Regulatory Guide 1.21 requirements. Equipment operation is not cffected by the ODCM, therefore malfunctions of equipment important to safety of a different type than previously evaluated in the SAR is not possible. P:rt IV: These changes incorporated by this revision to the ODCM bring the ODCM in compliance with Regulatory Guide 1.21 requirements and Technical Specifications. These changes will not reduce the margin of safety defined in the basis for any Technical Specification. Gaseous effluents from CPS are released on both a batch and continuous basis. Gaseous effluents are normally discharged on a long term basis. The changes implement Regulatory Guide 1.21, Section C.5 rIquirements for calibrating continuous monitors using comparisons against analysis of specific rldionuclides. ' There are two gaseous offipent release points to the environment: the Common StackHVAC Stack cnd the Standby Gas Treatment System (SGTS) Stack. The SGTS is an Engineered Safety Feature filter system utilized following an accident to reduce lodine 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 inputs. { l
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CPS-ODCM I ILLINOIS POWER COMPANY i DOCUKDIT Cnf 3 TROL APR 0 71998 l FOR REFEflENCE CLINTON POWEft STATION ILLINOIS POWER COMPANY CLINTON POWER STATION UNIT 1 OFFSITE DOSE CALCULATION MANUAL Docket No. 50-461 e. 4 i ? Ji2 LanoIa FRG 5 G h /12bz/97 () g % Date
/ ()
h /2 - /3- 1) Manager-ClintgGVPower Station Date I
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i i (LLINOIS POWER COMPANY DOCUf/~NT CONTROL DEC 1 O99'/
. CONTROL 0 COPY CLINTON POWER STATION CLINTON-1 Rev.16-12/97
CPS-ODCM Illinois Power Company Clinton Power Station OFFSITE DOSE CALCULATION MANUAL
)
. Table of Contents Section Title Page
- 1. 0 PREFACE 1-1 1.1 Definitions 1-1 1.2 General Operation Requirements 1-4 1.3 General Surveillance Requirements 1-4 1.4 Effluent Concentration Limit (lim) 1-6 Calculation Requirements 2.0 LIQUID EFFLUENTS 2.1 Introduction 2-1 1
2.2 Liquid Radwaste Discharge Process' 2-1 Radiation Monitoring (PRM) System 2.3 10CFR20 Release Rate Limits 2-1
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2.3.1 Liquid Effluent Concentration - 2-2 Operation and Surveillance Requirements 2.3.2 Liquid Radwaste 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 2.3.6 Component Cooling Water PRM 2-12 Setpoints iti.tNOtS POWErt COfAPANY DOCUME,[4T cot 4 TROL DEC 1 UW c O n lit 000 "
I' CLINTON POWER STATION CLINTON-1 i Rev.16-12 / 9'7
CPS ,ODCM Illinois Power Company Clinton Power Station r-( OFFSITE DOSE CALCULATION MANUAL 1 Table of Contents Section Title Page 2.0 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 2.4.2 Discussion 2-14 2.5 Liquid Radwaste Treatment System - 2-24 2.5.1 Liquid Radwaste Treatment , System - Operation and 2-24 Surveillance Requirements j 2.5.2 Temporary Liquid Radwaste 2-25 Hold-up Tanks 2.6 Doses From Other Significant Liquid (' Effluent Pathways 2-25 S 2.7 Radioactive Liquid Effluent Monitoring 2-25 Instrumentation 1 2.7.1 Radioactive Liquid Effluent 2-25 Monitoring Instrumentation- . Operation and Surveillance Requirements 3.0 GASEOUS EFFLUENTS 3-1
. 3.1 Introduction 3-1
. 3.2 Gaseous Effluent Release. Point Monitoring 3-2 , i 3.2.1 HVAC Stack Process Radiation 3-2 ! Monitoring (PRM) System
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3.2.2 SGTS Stack Process Radiation 3-2 Monitoring (PRM) System O e e es 41spe es ee b i- en e * * *$ e che
CPS-ODCM Illinois Power Company Clinton Power Station OFFSITE DOSE CALCULATION MANUAL
. Table of Contents Section Title Page 3.0 3.3 Main Condenser Off-Gas Monitoring System 3-3 3.3.1 Pre-Treatment Air Ejector 3-3 Off-Gas PRM '
3.3.2 Post-Treatment Air Ejector 3-4 Off-Gas PRM 3.4 10CFR20 Release Rate Limits 3-4 3.4.1 10CFR20 Release Rate Limits - 3-4 operation and Surveillance Requirements 3.4.2 Dose Rate Due to Noble Gases 3-9 3.4.3 Dose Rate Due to Radioiodines, 3-9 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 - Operations and Surveillare.c Requirements 3.5.3 Noble Gas Air Dose Equations 3-17 3.5.4 Radioiodines, Particulates.and 3-18 Tritium Dose Equations 3.6 Gaseous Radwaste (Offgas) Treatment 3-25 3.6.1 Gaseous Radwaste (Offgas 3-25 I
Treatment) System - Operation and Surveillance Requirements CLINTON-1 iii Rev.16-12/97 i i
I l l l CPS-ODCM Illinois Power Company l Clinton Power Station r~ l OFFSITE DOSE CALCULATION MANUAL ! Table of. Contents l Section Title Page 3.0 3.7 Ventilation Exhaust Treatment 3-27 3.7.1 Ventilation Exhaust Treatment 3-27 System - Operation and Surveillance Requirements 3.8 Effluent Monitor Setpoint Calculations 3-28 3.8.1 Total Body Dose Rate Setpoint 3-28 3.8.2 Skin Dose Rate Setpoint 3-30 3.9 Radioactive Gaseous Monitoring 3-31 Instrumentation
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3.9.1' Offgas Radiation Monitoring 3-31 Instrumentation - Operation and Surveillance Re'quirements /, 3.9.2 Radioactive Gaseous Effluent 3-38 Monitoring Instrumentation - Operation and Surveillance Requirements 4 .' O COMPLIANCE WITH 40CFR190 4-1 1 4.1 Total Dose - Operation and Surveillance 4-1 j Requirements I 4.1.a Special Report Requirements 4-1
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5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM 5-1 5.1 Monitoring Program - Operation and 5-1 Surveillance Requirements 5.2 Land Use Census - Operation and 5-21 Surveillance Requirements l
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CPS-ODCM Illinois Power Company Clinton Power Station OFFSITE DOSE CALCULATION MANUAL
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Table of Contents Section Title Page 5.0 5.3 Interlaboratory Comparison Program 5-22 5.3.1 Interlaboratory Comparison 5-23 Program - Operation and Surveillance Requirements 6.0 BASES FOR OPERATION AND SURVEILLANCE 6-1 REQUIREMENTS. 6.1 General Operation and Surveillance 6-1 Requirements i 6.2 Monitoring Instrumentation 6-2' 6.3 Radioactive Effluents 6-3 6.3.1 Liquid Effluents 6-3 ' 6.3.2 Gaseous Effluents 6-5
# 6-9 6.3.3 Total Dose 6.4 Radiological Environmental Monitoring 6-10 7.0 REPORTING REQUIREMENT $~ 7-1 7.1 Annual Radiological Environmental 7-1 Operating Report 7.2 Radioactive Effluent Release 7-2 Report 0.0 ADOUSTMENT OF THE CPS ODCM METHODOLOGY . 8-1 9.0 ATMOSPHERIC TRANSPORT AND DISPERSION MODEL 9-1 9.1 Introduction 9-1 l
1 CLINTON-1 ( v Rev.16-12/97
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CPS-ODCM Illinois Power Company Clinton Power Station ~* OFFSITE DOSE CALCULATION MANUAL 1 Table of. Contents Section Title Page 9.0 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 9-3 Wind Speed 9.2.3 Determination of Release Mode 9-3 and the Entrainment Coefficient 9.2.4 Calculation of Vertical Standard 9 Deviation i 9.2.5 Calculation of the Building Wake 9-5 Correction 9.2.6 Calculation of Momentum Plume 9-5 l Rise , 9.2.7 Calculation of Effective Plume 9-6 Height
- 9.2.8 Determination of Affected 9-7
, Sectors 9.2.9 Calculation of Depletion and 9-8 Deposition Factors 9.2.10 Ground Level X/Q, D2DPXQ, D1XQ, 9-12 D/O. Analysis 9.2.11 Elevated X/Q, D2DPXQ, D1XQ, D/O 9-13 Analysis e m
f j 1 i CPS-ODCM l Illinois Power Company I Clinton Power Station OFFSITE DOSE CALCULATION MANUAL Tables Table Title Page 1.1-1 Surveillance Frequency Notation 1-6 2.3-1 Radioactive Liquid Waste Sampling and Analysis 2-3 Program 2".4-1 Adult Ingestion Dose Commitment Factors - A33 2-16 2.4-2 Bioaccumulation Factors - BFi 2-18 2.4-3 Adult Ingestion Dose Factors - DFi 2-19 2.7-1 Radioactive Liquid Effluent Monitoring 2-27 * ' Instrumentation 2.7-2 Radioactive Liquid Effluent Monitoring 2-30 Instrumentation Surveillance Requirements 3.4-1 Radioactive Gaseous Waste Sampling and Analysis 3-6 Program
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3.4-2 Dose Factors for Noble Gases and Daughters 3-11 3.4-3 Inhalation Pathway Dose Rate Factors (Child) - 3-12 Pi3 3.4-4 Location of Members of the Public Within the 3-14 CPS Site Boundary and Their Associated Occupancy Factors 3.9.1-1 Offgas Radiation Monitoring Instrumentation 3-32 3.9.1-2 Offgas Radiation Monitoring" Instrumentation 3-36 Surveillance Requirements , 3.9.2-1 Radioactive Gaseous Effluent Monitoring 3-39 Instrumentation 3.9.2-2 Radioactive Gaseous Effluent Monitoring 3-41 Instrumentation Surveillance Requirements , 3.5-1 Inhalation Dose Factors for Infant-(DEA ). i 3-45
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3.5-2 Inhalation Dose Factors for Child-(DEAg). 3-47 3.5-3 Inhalation Dose Factors for Teen-(DEA ). 1 3-49 l r 7.rumu 1 ,,4 4 n ~. 1e_,oin,
CPS-ODCM Illinois Power Company Clinton Power Station {"
.OFFSITE DOSE CALCULATION MANUAL Tables Table Title Page 3.5-4 Inhalation Dose Factors for Adult-(PA ). i 3-51 3.5-5 Ground Plane Dose Factors-DFG i 3-53 3.5-6 Ingestion Dose Factors for Infant-(OFL ).1 3-55 l 3.5-7 Ingestion Dose Factors for Child-(DFL ). 1 3-57 3.5-8 Ingestion Dose Factors for Teen-(D% ). i 3-59 3.5-9 Ingestion Dose Factors for Adult-(DFL ).1 3-61 3.5-10 Input Parameters for Calculating R.13 3-63 3.5-11 Input Parameters for Calculating R".13 3-64 V
3.5-12 Input Parameters for Calculating'R.13 3-65 3.5-13 Inhalation Pathway Factors - R*.13 (INFANT) 3-66 ( 3.5-14 Inhalation Pathuay Factors - R.13 (CHILD) I 3-68 3.5-15 Inhalation. Pathway Factors - R*.13 (TEEN) 3-70 3.5-16 Inhalation Pathway Factors - R*.13 (ADULT) _ 3-72 3.5-17 Cow Milk Pathway Factors - R.13 (INFANf) 3 74 C 3.5-10 Cow Milk Pathway Factors - R.13 (CHILD) 3-76 3.5-19 Cow Milk Pathway Factors - R*.13 (TEEN) 3-78 3.5-20 Cow Milk Pathway Factors - R .13 (ADULT) 3-80 3.5-21 Goat Milk Pathway Factors - R.13 (INFANT) 3-82 3.5-22 Goat Milk Pathway Factors - R".13 (CHILD) 3-84 3.5-23 Goat Milk Pathway Factors - R*.s3 (TEEN) 3-86 3.5-24 Goat Milk Pathway Factors - R".f3 (ADULT) 3-88 l 3.5-25 Meat Pathway Factors - R".13 (CHILD) 3-90 3.5-26 Meat Pathway Factors - R".33 (TEEN) 3-92 3.5-27 Meat Pathway Factors - R".13 (ADULT) 3-94
t CPS-ODCM Illinois Power Company Clinton Power Station OFFSITE DOSE CALCULATION MANUAL Tables Table Title Page V 3.5-28 Vegetation Pathway Factors - R.13 (CHILD) 3-96 3.5-29 Vegetation Pathway Factors - R*.33 (TEEN) 3-98 V 3.5-30 Vegetation Pathway Factors - R.13 (ADULT) 3-100 l l 3.5-31 Gr'und o Plane Pathway Factors - R"i 3-102 j 5.1-1 Radiological Environmental Monitoring Program 5-4 5.1-2 Reporting Levels for Radioactivity 5-17 Concentrations in Environmental Samples ! 5.1-3 Detection Capabilities for Environmental Sample 5-18 Analysis Lower Limit of Detection 9.2-1 Gaseous Effluent Release Point Characteristics 9-15
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CLINTON.1 ix Rev.16-12/97
CPS-ODCM ,
' Illinois Power Company Clinton Power Station
{" OFFSITE DOSE CALCULATION MANUAL i Figures Figure Title Page 2.1-1 Unrestricted Area Boundary for Liquid Effluents 2-10 2.5-1 Liquid Radwaste Treatment System 2-21 2.5-2 Shutdown and Fuel Pool Heat Exchanger Service 2-22 Water Effluent Monitors' - 2.5-3 Solid Radwaste System Simplified Flow Diagram 2-23 3.1-1 CPS Site Boundary For Gaseous Effluents 3-43 3.3-1 Main Condenser Off-Gas Treatment System 3-44 5.0-1 REMP Locations Within 1 Mile of CPS 5-24 5.0-2 REMP Location 1-2 Miles From CPS 5-25 5.0-3 REMP Location 2-5 Miles From CPS 5-26 5.0-4 REMP Locations Greater than 5 Miles From CPS 5-27 ( , i l i e
i ( CPS-ODCM f 1.0 GENERAL INFORMATION PREFACE
') The Clinton Power Station OFFSI13 DOSE CALCULATION MANUAL (CPS-ODCM) provides the methodologies and parameters to be used by Illinois Power Company (IPC) to assure compliance with the radioactive effluent dose limitations l stated in 10CFB20, 10CFR50 Appendix A (General Design Criteria 60 anc 64), 10CER50 Appendix I, and 40CFR190.
l ! The CPS-ODCM was prepared based on guidance provided in l NUREG-0133, PREPARATION OF RADIOLOGICAL EFFLUENT TECHNICAL SPECIFICATIONS FOR NUCLEAR POWER PLANTS l (October 1978), and NUREG-0473, RADIOLOGICAL EFFLUENT TECHNICAL SPECIFICATIONS FOR BOILING WATER REACTORS (Draft 7, to Revision 3). This manual along with station procedures will be used by CPS personnel to demonstrate compliance with the above referenced Federal Regulations. Changes to the CPG-ODCM shall be provided in the RADIOACTIVE EFFLUENT 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 j and shall be applicable throughout this manual. CHANNEL CALIBRATION 1.1.1 A CHANNEL CALIBRATION shall be the adjustment, as necessary, of the channel output such that it responds with the necessary range and accuracy to known values of the parameter that the channel monitors. The CHANNEL CALIBRATION shall encompass the entire channel, including the required sensor, alarm, display, and trip functions,
, and shall include the CHANNEL FUNCTIONAL TEST.
Calibration of instrument channels with resistance temperature detector (RTD) or thermocouple sensors may consist of.an in place qualitative assessment of sensor behavior and normal calibration of the remaining adjustable devices in the channel. The CHANNEL CALIBRATION may be performed by means of any series of sequential, overlapping or total channel step.s so that the entire channel is calibrated. CLINTON-1 1-1 Rev.16-12/97
CPS-ODCM
- CHANNEL CHECK r
f. 1.1.2 ' A CHANNEL CHECK shall be the qualitative assessment of channel behavior during operating by observation. This I determination shall include, where possible,, comparison of the channel indication'and/or status with other indications and/or status derived from independent instrument channels measuring the same parameter. CHANNEL FUNCTIONAL TEST
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1.1.3 A CHANNEL FUNCTIONAL TEST shall be the injection of a simulated, or actual, signal into the channel as close to . the sensor as practicable to verify OPERIiBILITY, including required alarm, interlock, display, and trip functions, and channel failure trips. The CHANNEL FUNCTIONAL TEST may be performed by means of any series of sequential, overlapping or total channel steps so that the entire channel is tested. FREQUENCY NOTATION 1.1.4 The FREQUENCY NOTATION specified for the performance of surveillance requirements shall correspond to the intervals defined in Table 1.1-1. GASEOUS 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 system and providing for delay or holdup for the purpose of reducing the total radioactivity prior to release to the environment. MEMBER (S) OF THE PUBLIC 1.1.6 An individual in a controlled or unrestricted area. However, an individual is not a member of the public during any period in which the individual receives an occupational dose. 1.1.6a MODE A MODE shall correspond to any one inclusive combination of mode switch position, average reactor coolant temperature, and reactor vessel head bolt tensioning specified in Technical Specification Table 1.1-1 with fuel in the reactor vessel. . 1
CPS-ODCM OPERABLE - OPERABILITY 1.1.7 A system, subsystem, division, component or device shall be OPERABLE or have. OPERABILITY when it is capable of
) performing its specified safety f.tnction(s) and when all necessary attendant instrumentation, controls, normal or emergency electrical power, cooling' or seal water, lubrication or other auxiliary equipment that are required for the system, subsystem, division, component or device to perform its specified safety function (s) are also capable of performing their related support function (s) .
REMEDIAL REQUIREMENT 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. i SOURCE CHECK 1.1.10 A SOURCE CHECK shall be the qualitative assessment of f channel response when the channel sensor is exposed to a source of increased radioactivity. UNRESTRICTED AREA 1.1.11 An UNRESTRICTED AREA means an area, access to which is neither limited nor, controlled by the licensee. 1 VENTILATION EXHAUST TREATMENT SYSTEM 1.1.12 A VENTILATION EXHAUST TREATMENT SYSTEM is any system designed and installed to reduce gaseous radioiodine or radioactive material in particulate form in effluents by
. passing ventilation or vent exhaust gases through charcoal adsorbers and/or HEPA filters for the purpose of removing iodines or particulates from the gaseous exhaust stream prior to the release to the environment. Such a system is not considered to have any effect o,n noble gas effluents. Engineered Safety Feature (ESF) atmospheric cleanup systems are not considered to be VENTILATION EXHAUST TREATMENT SYSTEM components.
CLINTON-1 1-3 Rev.16-12/97
CPS-ODCM The following systems are designated VENTILATION EXHAUST TREATMENT SYSTEMS: g-5
- 1) Machine Shop HVAC (VJ) )
- 2) Laboratory HVAC (VL) ,
1
- 3) Drywell Purge (VQ)
- 4) Radwaste Bldg HVAC (VW) 1.2 General Operation Requirements
, 1.2.1 Operation Requirements shall be met during the conditions specified therein; except as provided in Operation Requirement 1.2.2. - 1.2.2 Upon discovery of a failure to meet an Operation Requirement, the REMEDIAL REQUIREMENT (s) shall be met, except as provided in 1.2.3. If the Operation Requirement is met or is no longer applicable prior to expiration of the REMEDIAL 1 REQUIREMENT (s), completion of the REMEDIAL REQUIREMENT (s) i is not required, unless otherwise stated. 1.2.3 Equipment removed from service or declared inoperable to comply with REMEDIAL REQUIREMENT (s) may be returned to [ service under administrat'ive control solely to perform l testing required to demonstrate OPERABILITY or the l OPERABILITY of other equipment. This is an exception to OPERATION REQUIREMENT 1.2.2 for the system returned to j service under administrative control to perform the ! testing required to , demonstrate OPERABILITY. 1.3 General Surveillance Requirements 1.3.1 Surveillance Requirements shall be met during the applicable conditions specified in and for the associated Operation Requirement, unless otherwise stated in the' ' Surveillaince Requirement. Failure to meet a Surveillance, whether such failure is experienced during the performance of the surveillance, or between performances of the Surveillance, shall be failure to I meet the Operation Requirement. ; Ah even.mu 4 _, . . . . - - - , - -
CPS-ODCM 1.3.2' The specified surveillance interval for each Surveillance Requirement is met if the Surveillance is performed within 1.25 times the specified surveillance interval, as measured from the previous performance or as measured I from the time a specified condition of the Surveillance Requirement is met. For surveillance intervals specified as "once", the above interval extension does not apply. If a REMEDIAL REQUIREMENT requires periodic performance on a "once per ... " basis, the above surveillance interval extension applies to each performance after the initial performance. Exceptions to this Surveillance Requirement are stated in the individual Surveillance Requirements. Failure to perform a surveillance within the specified time interval shall be a failure to meet the Operation Requirement except as provided in Surveillance Requirement 1.3.3. Surveillances do not have to be performed on inoperable equipment or variables outside specified limits. 1.3.3 If it is discovered that a surveillance was not performed within its specified surveillance interval, then compliance with the requirement to declare.the / Operational Requirement not met may be delayed, from the time of discovery, up to 24 hours or up to the limit of the specified interval, which ever is less. This delay period is to allow performance of the surveillance. If the surveillance is not performed within the delay period, the Operational Requirement must immediately be declared not met', and the applicable REMEDIAL REQUIREMENTS must be met. 1.3.4 Entry into a condition specified in and for an Operation Requirement 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. This provision shall not prevent entry into conditions specified for an Operation Requirement that is required to comply with REMEDIAL REQUIREMENT (s) or that are part I of a shutdown of the unit. Surveillance Requirement 1.3.4 is only applicable for entry into a condition specified for an Operation Requirement in MODES 1, 2, and 3. CLINTON-1 1-5 Rev.16-12/97
1 I CPS-ODCM 1.4 Effluent Concentration Limit (lim) Calculation Requirements f-1.4.1 The values found in 10CFR20 Appendix B, Table 2, Column 2 ; shall be used for all lim calculations in the ODCM. TABLE 1.1-1
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l SURVEILLANCE FREQUENCY NOTATION NOTATION FREQUENC.Y S At least once per 12 hours. D At least once per 24 hours. 1 W At least once per 7 days. M At least once per 31 days. O At least once per 92 days. SA At least once per 184 days. ( A At least once per 366 days. R At least once per 18 months (550 days) P Prior to each release. S/U P,rior to each reactor startup. NA Not applicable. Note: A frequency notation for a composite sample describes the time period over which the sample is to be ) composited. i l
=
O
CPS-ODCM 2.0- LIQUID EFFLUENTS- 4 2.1 Introduction l ] Liquid radwaste effluent released from CPS will meet l 10CFR20 concentration limits at the point of discharge to the unrestricted area shown in Figure 2.1-1. This_ design l and operation objective will be achieved at all times. I Actual discharges of liquid radwaste effluent wil1 normally occur on a batch basis and the average concentration at the point of discharge will be only a small percentage of the allowed limits. Refer to Clinton ! USAR Section 11.5 for a description of radiation l l monitoring, sampling and effluent control systems. Cumulative quarterly dose contributions due to radioactive effluents. released to the unrestricted area will be determined once every 31 days using NUREG-0133 and Regulatory Guide 1.109 methodology and parameters. l 2.2 Liquid Radwaste Discharge Process Radiation Monitoring ' (PRM) System This monitoring subsystem measures liquid radwaste effluent radioactivity prior to the effluent joining plant service water and circulating water dilution ! streams. A high radioactivity signal from this gamma scintillation detector automatically terminates the t ~j liquid radwaste effluent release.. The liquid radwaste effluent flow, variable from 10-60 GPM or 50-300 GPM, combines with Plant Service Water flow (minimum flow approximately 2000 GPM during plant shutdown periods depending on s.ystem loads) and Plant Circulating Water flow (0-567,000 GPM) in the Seal Well prior to entering the 3.4-mile discharge flume to Lake Clinten (see Figure 2.5-1). 2.3 10CFR20 Release Rate Limits The Operation and Surveillance Requirements pertaining to discharge'of liquid radwaste effluent to the unrestricted area are specified in Section 2.3.1 as follows. h CLINTON-1 2-1 Rev.16-12/97
[ l - i CPS-ODCM l 2.3.1 Liquid Effluent concentration - Operation and Surveillance Requirements e i . OPERATION REQUIREMENT ! Th'e concentra' tion of radioactive material released in liquid effluent to UNRESTRICTED AREAS (see Figure 2.1-1) shall be limited to ten times the concentrations specified in 10CFR Part 20, Appendix B, Table 2, Column 2 for radionuclides other than dissolved or entrained noble gases. For dissolved or entrained noble the concentration shall be limited to 2 x 10" gases, microcuries/ml total activity. This requirement applies during all - releases via this pathway. . REMEDIAL REQUIRFEENT: With the concentration of radioactive material released in liquid effluents to UNRESTRICTED AREAS exceeding the above limits,.immediately restore the concentration to within the above limits. SURVEILLANCE REQUIREMENTS 2.3.1.1 Radioactive liquid wastes shall be sampled and analyzed according to the sampling and analysis program of Table 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 assure that the concentrations at the point of release are maintained within the limits of the above Operation Requirement. To comply with the above requirements, setpoints will be
~
calculated to assure that Seal Well concentrations do not exceed 10CFR20, Appendix B, Table 2, Column 2 values at any time. O i-
l CPS-ODCM TABLE 2.3-1 , y RADIOACTIVE LIQUID WASTE SAMPLING AND ANALYSIS' PROGRAM LOWER LIMIT LIQUID MINIMUM OF DETECTION RELEASE SAMPLING ANALYSIS TYPE OF ACTIVITY' (LLD)* TYPE FREQUENCY FREQUENCY ANALYSIS ( Ci/ml) l Batch Waste P P Principal Gamma 5x10-7 i Release Each Batch Each Batch Emitters
- Tanks b ~
I-131 1x10-6 P M Dissolved and 1x10-5 One Batch /M Entrained Gases * ! (Gamma Emitters) P Q H-3 1x10-5 Each Batch Composite d j , Gross Alpha 1x10-7' P Q Sr-89, Sr-90 5x10-8 Each Batch ' Composite d Fe-55 1x10-6' i l l CLINT 1 2-3 nov.1 g_12 /97
1 I CPS-ODCM l TABLE 2.3-1 (Continued) RADIOACTIVE LIQUID WASTE SAMPLING AND ANALYSIS PROGRAM TABLE NOTATIONS
'The 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 false]y concluding that a blank observation represents a "real" signal. For a particular measurements system, which may include i radiochemical separation: l LLD = 4. 66 sb/ [E x V x 2.22 x 10' x Y x exp'~ A"] Whore: LLD is the "a priori" lower limit of detection as defined above, as microcuries per unit mass or volume, se is the standard deviation of the background counting rate or of the counting rate of a blank sample as appropriate, as counts per minute. y E is the counting efficiency, as counts per disintegration, # V is the sample size in units of mass or volume, 2.22 x 10' is the number of disintegrations per minute per microcurie, Y is the fractional radiochemical yield, when applicable, 1 is the radioactive decay constant for the p' articular radionuclide ( s e c-* ) and At for plant effluents is the elapsed time between the midpoint of sample collection and the midpoint of the counting interval (sec). Typical values of E, V, Y and At should be used in the calculation.
~
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CPS-ODCM TABLE'2.3-1 (Con'tinued) RADIOACTIVE LIOUID WASTE SAMPLING AND ANALYSIS PROGRAM
) TABLE NOTATIONS (Continued)
It should be recognized that the LLD is defined as an a priori q (before the fact) limit representing the capability of a measurement system and not as an a posteriori (after the' fact) limit for a particular measurement.
'A 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. ,
)
- The principal gamma emitters are: Mn-54, Fe-59, Co-58, Co-60, Zn-65, Mo-99, Cs-134, Cs-137, and Ce-141. Ce-144 shall also be measured, but with an LLD of 5 x 10-6 pCi/ml. All identified radionuclides.shall be reported in the Radioactive Effluent Release Report pursuant to Technical Specification 5.6.3 in a format outlined in Regulatory Guide 1.21, Appendix B, Revision 1, June 1974.
- A composite sampie 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.
/
- Dissolved and Entrained gases are: Xe-133, Xe-135, Xe-138, Kr-85m, Kr-87, and Kr-88.
l I ( I l l CLINTON-1 2-5 Rev.16-12/97
I l I l, ' CPS-ODCM , 2.3.2 Liquid Radwaste Discharge PRM Setpoints To comply with the Operation Requirements of Section i 2.3.1 and Section 2.7.1, the alarm / trip setpoints for ! liquid effluent monitors and flow measurement devices are set to assure that the following equation is satisfied: cf/ (F + f) < Cum (1) Cn. =
- the effluent concentration limit (section
! 2.3.1) implementing 10CFP20 for the site, corresponding to the specific mix of ra'dionuclides 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 li,ne 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 effluent stream.
~
F = the dilution water flow setpoints as f determined'at the Seal Well, in volume per 1 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 di'scharge flow (f) and monitor setpoint (c) are set to meet the condition of equation (1) for a given effluent concentration (Cn.). The method by which this is accomplished is illustrated in sections 2.3.2.1 through 2.3.2.5. 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
l W 9
CPS-ODCM- , esc =E,C,+ E.C.+ E.C.+ Cr+ Cr. , pCi/ml i (2) where
) E,C, = The sum of concentrations C, of each measured gamma emitter g (including I-131) observed by gamma spectroscopy of the waste sample, Ci/ml.
E.C. = The sum of concentrations C, of' alpha einitters (a) in liquid radwaste as measured in the-most-
-current-QUARTERLY composite discharge tank sample, pCi/ml.
I.C. = The sum of concentrations C, of Sr-89/Sr-90 in liquid radwaste as observed in the most" current QUARTERLY composite discharge tank sample, pCi/ml. C, = The measured concentration of H-3 in liquid radwaste as determined from analysis of-the , most current QUARTERLY composite discharge tank sample, pCi/ml. Cr. = The measured concentration of Fe-55 in liquid radwaste as observed in the most current QUARTERLY composite discharge tank sample, pCi/ml. r 2.3.2.2 The measured radionuclide concentrations are used to i calculate a DILUTION FACTOR (DF) which is equivalent to j the ratio of total dilution flow rate to liquid I radwaste tank effluent flow rate required to assure that the limiting concentrations of 10CFR20, Appendix B, Table 2, Column 2 are met at the point of discharge to the unrestricted area. l DF = SF[Ei (Ci /limi) ] , dimensioaless (3)
= sr(E,(c,/11m,)+I.(c./ lim.) +I (c./ lim He /11m r ) +c r / lim r .)] r where -
ECii = The measured concentratit.ns C,, C., C., C,, Cre as defined in equati:,n (2), pCi/ml. 1 i limi = The limiting concentration of the orresponding radionuclide from 10CFR20, Appendix B, Table 2, Column 2, Ci/ml. For dissolved or entrained noble gases, the concentration shall be limited to 2E-04 Ci/ml total activity. l I ('T.TM PAM-1 ?-7 n a.. 1 c _1 o '/ 0 7
I CPS-ODCM 4 SF = The conservative SAFETY FACTOR normally applied to compensate for statistical fluctuations and (~ measurement errors, dimensionless. \ l ! 2.3.2.3 The maximum permissible liquid radwaste tank effluent ! flow rate, Ft .nx, equation: is'ca'lculated by the following F .nx =0.9(Fo1+ f .nn) /DF, volume / time t t (4) where Fud = Minimum expected dilution water flow rate (Circulating and/or Service Water systems), volume / time
.f t.nx =
Maximum expected liquid radwaste tank effluent flow rate, volume / time 0.9 = Flow rate correction factor to provide a 10% margin for variations in flow rates, dimensionless DF = The DILUTION EACTOR calculated by equation (3), dimensionless Equation (4) is valid only for DF>1; for DF<1, the (. liquid radwaste tank effluent concentration meets the ' limits of,10CFR20 without dilution and therefore F.nw t 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 1C i (Eq.2) and F.ng t (Eq.4) which were determined to provide compliance with the concentration limits of 10CFR20, Appendix B, Table 2, Column 2. The monitor response is primarily a gamma response and the actual setpoint is therefore based on Eg C, (Eq.2). The monitor setpoint, in counts per I minute (cpm), which corresponds to the particular setpoint concentration, Cu, 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 lf the j integrity of laboratory methods of determination are ' proven more accurate than the monitor data. l
i CPS-ODCM ! The set point concentration,'Cs, is obtained by the following equation: g Cs = [ Ft .ng/ f.et ] gE gC , pCi/ml (5) l where , f.et = The actual liquid radwaste effluent flow rate, i volume / time i j If ( F .ng/ t f.ct ) >1, the value obtained for Cs is used to determine the monitor setpoint above background, ccpm, l from either of the two methods described above. In the case where (F .ng/f.et) t <1, no release may be made using the existing discharge parameter values (DF, Pt .nk, f.ct)
- l The setpoint concentration is conservative, even if Ft .nw is attainable, since tha. calculated flow rate contains the SAFETY EACTOR, dilution flow rate and -
li, quid radwaste tank effluent flow rate margins. ! 2.3.2.5 To prevent spurious alarms, revise the Plant Service
- l Water Effluent PRM setpoint to coincide with the setpoint concentration, Cw, calculated by equation (5).
This.setpoint is valid only during periods of actual
- liquid radwaste discharges.
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CPS-ODCM 2.3.3 Plant Service Water Effluent PRM Setpoints l Plant service water effluent continuously releases to
) the Seal Well where it' mixes with circulating water effluent (if . present) prior to entering Lake Clinton via the 3.4 mile discharge flume. The plant service water effluent is not considered a radioactive discharge pathway unless liquid radwaste dischsrges are l in progress or any service water cooling load heat exchanger has been detected as failed. To ensure that Pl' ant 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-emitting radionuclides. In addition, a quarterly composite of positive grab samples 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.
The Plant Service Water effluent PRM setpoint should be established as close.to background as practical to prevent spurious alarms, and yet assure an alarm should an inadvertent release occur. If the weekly grab sample analysis indicates the j presence of contamination above background, PRM setpoints will be established following section 2.3.2 methodology as follows: 2.3.3.1 Perform section 2.3.2.2, solving 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, DF., must be determined so that available dilution flows may be apportioned among simultanecus discharge pathways. The modified dilution factor is defined as:
. DF. =
DF/Fx (6) where Fx is an administrative allocation factor which may be assigned any value between 0 and 1 under the condition that l CLINTON-1 2-11 Rev.16-12/97
CPS-ODCM , En ( Fa) n <1 (7) l and where n = the number.of liquid discharge pathways for which DF >1^and which are planned for simultaneous release. For simplicity, Fa may be assigned the value 1/n. Calculate Ft .nx in equation (4) by substituting the value of DF, for DF and perform the calculation l specified in section 2.3.2.4 to determ.ine flow . rate and
-PRM setpoints. )
a l 2.3.4- Shutdown Service Water (SX) Effluent PRM Setpoints Shutdown Service Water, when initiated,'is a potential l continuous radioactive discharge pathway'to the l Ultimate Heat Sink'(UHS) (see Figure 2.5-2). The SX effluent is not considered a radioactive discharge _ pathway unless any SX cooling load heat exchanger has l been detected as failed. SX effluent sampling, analysis and setpoint 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 Setpoints The Fuel Pool Heat Exchanger Service Water is normally supplied by the Component cooling Water (CCW) system (a closed loop system). The CCW system rejects heat loads i to the Plant Service Water system where intersystem leakage would be detected as described in section 2.3.3. The Fuel Pool Heat Exchanger Service Water ! effluent is considered a potential radioactive l-discharge pathway when SX replaces CCW as the heat sink l for the fuel pool heat exchangers. To account for a potential release of CCW radioactivity to the Ultimate Heat Sink via SX, CCW will be sampled prior.to placing the Fuel Pool Heat Exchanger in the SX cooling mode and l analyzed as discussed in section 2.3.3. The analysis i results will then.be used to establish Fuel Pool Heat Exchanger Service Water PRM and flow rat'e setpoints following Section 2.3.3.1 and 2.3.3.2 methodology. July releases of radioactivity to the environment. from i the Plant Service Water (except during liquid radwaste discharges), shutdown Service Water or FueA Pool Heat Exchanger Service Water Systems are considered abnormal events. Such events will be accounted for as unplanned releases in the RADIOACTIVE EFFLUENT RELEASE REPORT. 2.3.6 Compon'ent Cooling Water PRM Setpoints The Component Cooling' water system is a potential I continuous radioactive discharge pathway to the Service ! Water system due to the Component Cooling water system generally operating at a higher pressure. Component Cooling provides cooling to components and heat exchangers that carry radioactive fluids of are in areas that could result in radioactive contamination if the components are damaged. Except for the sampling requirement described in 2.3.5, sampling on this system is done on an as needed basis. The PRM setpoints are established using the methodology in Section 2.3.3.
CPS-ODCM 2.4 10CFRSO, Appendix I Release Rate Limits The Operation and Surveillance Requirements concerning 10CFR50, Appendix I Release Limits are specified in i section 2.4.1. Dose calculations for ensuring compliance.with these limits are discussed in section 2.4.2. 2.4.1 10CFR50, Appendix I Release Rate Limits - Operation and Surveillance Requirements OPERATION REQUIREMENT The dose or dose commitment to a MEMBER OF THE PUBLIC from radioactive materials in liquid effluents released to UNRESTRICTED AREAS (see Figure 2.1-1) shall be limited:
- a. During any calendar quarter to less than or equal to 1.5 mrem to the total body and to less than or equal to 5 mrem to any organ, and
- b. During any calendar year to less than or equal to 3 mrem to the total body and to less than or equal to 10 mrem to any organ.
This requirement applies at all times. ) REMEDIAL REQUIREMENT: With the calculated dose from the release of radioactive materials in' liquid effluents 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 (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 sWbsequent releases will be in compliance with the above limits.
. SURVEILLANCE REQUIREMENTS 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.16-12/97
CPS-ODCM 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: D3 = E [A 13 I" AT,Cufe], mrem i (8) f=1 where D3 = The cumulative calendar quarter or yearly dose to any organ j from liquid effluent for the total release period, mrem - AT, = The length of the 4th release time period over which Cu and Et are averaged for liquid releases,' hours
= Liquid Radwaste Tank Volume / Liquid Radwaste Discharge Flow Rate Cu = The average concentration of nuclide i in undiluted liquid effluent during release period att for any liquid release, pci/ml
=
{ Et The near field average dilution factor for Cu ' during any liquid effluent release, dimensionless. Defined as 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
= Average Undiluted Liquid Waste Flow (9) l (Average Discharge Structure Flow)Z l Z = The applicable dilution factor for Lake Clinton, dimensionless
= ~1.0 l
A33
= The composite ingestion dose commitment factor j for the total body or critical organ of an !
ADULT for radionuclide i, mrem /hr per Ci/ml l
= Ko ( (0,/Dw) + (UgBF ) ] DFi i (10) i l
CPS-ODCM where Ko = A units conversion factor, 1.14E+05 pCi-ml-yr/ pCi-liter-hr
..I
= (1.0E+06 pCi/pC1) (1.0E+03 ml/11ter) /8760 hr/yr U, = Annual water consumption by the maximum. adult, 0 liter /yr D. =
Dilution factor.from the near field area to the nearest potable water intake, 1.0
= Adult fish consumption rate, 21 kg/yr (Table Ur E-5 of Regulatory Guide 1.109)
BFi = Bioaccumulation factor for radionuclide i in fish, pCi/kg per.pCi/ liter (Table 2.4-2 taken from Table A-1 of Regulatory Guide 1.109) DFs = Adult ingestion dose conversion factor for radionuclide 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 fer'A13 as calculated by equation (10).
) The quarterly limits specified in the OPERATION REQUIREMENT at the beginning of this section represent one-half of the annual design objective of Section II.A of 10CFR50, Appendix I.
l
] /
CLINTON-1 2-15 Rev .16-17 / 97
CPS-ODCM , TABLE 2.4-1 y. ADULT INGESTION DOSE COMMITMENT FACTORS - Au (mrem /hr per pCi/ml) ESOTOPE BONE LI'.*ER T. BODY THYROID KIDNEY LUNG GI-LLI H-3 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 6.24E+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 4.06E502 4.06E+02 P-32 1.39E+06 8.62E+04 5.36E+04 NO DATA NO DATA NO DATA 1.56E+05 CH-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 6.57E+02 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 NI-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 EN-65 2.31E+04 7.36E+04 3.33E+04 NO DATA 4.92E+04 NO DATA 4.64E+04 ZN-69 4.92E+01 9.42E+01 6.55E+00 NO DATA 6.12E+01 NO DATA 1.41E+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 RB-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 SR-91 5.43E+05 4.06E+02 NO DATA NO DATA 1.33E+05 1.64E+01 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA 1.57E+04 1.94E+03 [ SR-92 1.54E+02 NO DATA 6.67E+00 NO DATA NO DATA NO DATA 3.05E+03 Y-90 5.75E-01 NO DATA 1.54E-02 NO DATA NO DATA NO DATA 6.10E+03 Y-91m 5.43E-03 NO DATA 2.10E-04 NO DATA NO DATA NO DATA 1.60E-02 Y-91 8.42E+00 NO DATA 2.25E-01 NO DATA NO DATA NO DATA 4.64E+03 Y-92 5.05E-02 NO DATA 1.48E-03 NO DATA NO DATA NO DATA 8.84E+02 Y-93 1.60E-01 NO DATA 4.42E-03 NO DATA NO DATA NO DATA 5.08E+03 ZR-95 '2.40E-01 7.69E-02 5.20E-02 NO DATA 1.21E-01 NO DATA 2.44E+02 ER-97 1.32E-02 2.67E-03 1.22E-03 NO DATA 4.04E-03 NO DATA 8.28E+02 NB-95 4.46E+02 2.48E+02 1.33E+02 NO DATA 2.45E+02 NO DATA 1.51E+06 MO-99 NO DATA 1.03E+02 1.96E+01 NO DATA 2.33E+02 NO DATA 2.39E+02 TC-99m 8.86E-03 2.50E-02 3.19E-01 NO DATA 3.80E-01 1.23E-02 1.48E+01 TC-101 9.11E-03 1.31E-02 1.29E-01 NO DATA 2.36E-01 6.70E-03 3.94E-14 RU-103 4.42E+00 NO DATA 1.90E+00 NO DATA 1.69E+01 NO DATA 5.16E+02 RU-105 3.68E-01 NO DATA 1.45E-01 'NO DATA 4.76E+00 NO DATA 2.25E+02 RU-106 6.57E+01 NO DATA 8.32E+00 NO DATA 1.27E+02 NO DATA 4.25E+03 AG-110m NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA TE-125m 2.57E+03 9.20E+02 3.43E+02 7.70E+02 1.04E+04 NO DATA 1.02E+04 TE-127m 6.47E+03 2.31E403 7.89E+02 1.65E+03 2.63E+04 NO DATA 2.17E+04 TE-127 1.05E+02 3.77E+01 2.28E+01 7.79E+01 4.28E+02 NO DATA 8,30E+03 TE-129m 1.10E+04 4.10E+03 1.74E+03 3.78E+03 4.59E+04 NO DATA 5.54E+04 TE-129 3.00E+01 1.13E+01 7.31E+00 2.30E+01 1.26E+02 NO DATA 2.26E+01 TE-131m 1.65E+03 8.09E+02 6.74E+02 1.28E+03 8.19E+03 NO DATA 8.03E+04 TE-131 1.88E+01 7.87E+00 5.95E+00 1.55E+01 8.25E+01 NO DATA 2.67E+00 I
CPS-ODCM TABi;E 2.4-1 (cont'd) l ADULT INGESTION DOSE COMMITMENT FACTORS - Ag (mrem /hr per Ci/ml) ISOTOPE BONE LIVER T. BODY . THYROID KIDNEY LUNG GI-LLI TE-132 2.41E+03 1.56E+03 1.46E+03 1.72E+03 1.50E+04 NO DATA 7 . 37 E+ 04 I-130 2.71E+01 7.99E+01 3.15E+01 6.78E+03 1.25E+02 NO DATA 6.88E+01 I-131 1.49E+02 2.13E+02 1.22E+02 6.99E+04 3.66E+02 NO DATA 5.63E+01 I-132 7.28E+00 1.95E+01 6.81E+00 6.81E+02 3.10E+01 NO DATA 3.66E+00 I-133 5.09E+01 8.85E+01 2.70E+01 1.30E+04 1.54E+02 NO DATA 7.96E+01 I-134 3.80E+00 1.03E+01 3.69E+00 1.79E+02 1.64E+01 NO DATA 9.00E-03 "I-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+02 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 1.77E-04 1.18E-04 2.89E-19 LA-140 1.49E-01 7.53E-02 1.99E-02 NO DATA NO DATA NO DATA' 5.53E+03 LA-142 7.65E-03 3.48E-03 8.66E-04 NO DATA NO DATA NO DATA 2.54E+01 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 1.20E-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 . 5'9 E-10 ND-147 3.76E-01 4.34E-01 2.60E-02 NO DATA 2.54E-01 NO DATA 2.08E+03 W-187 2.95E+02 2.47E+02 0.63E+01 NO DATA NO DATA NO DATA 8.09E+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 10'
* *Less than 10-15 /
CLINTON-1 2-17 Rev.16-12/97
u CPS-ODCM , TABLE 2.4-2 BIOACCUMULATION FACTORS -BF3 (pCi/kg per pCi/ liter) FRESHWATER ELEMENT FISH H 9.0E-01 C 4.6E+03 Na 1.0E+02 P 1.0E+05 Cr 2.0E+02 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+0'3 Sr 3.0E+01 Y 2.5E+01 Zr 3.3E+00 Nb 3.0E+04 -
.Mo 1.0E+01 (
Tc 1.5E+01 , Ra 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 Pr 2.5E+01 Nd 2.5E+01 W 1.2E+03 Np 1.0E+01
.- ___.____m__-__
CPS-ODCM TABLE 2.4-3 ADULT INGESTION DOSE FACTORS -DFi (mrem /pCi ingested)
)
ISOTOPE DONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ' 11 - 8 NO DATA 1.05E-07 1.05E-07 1.05E-07 1.05E-07 1.05E-07 1.05E-D7 C-14 2.84E-06* 5.68E-07 5.6BE-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 l P-32 1.93E-04 1.20E-05 7.46E-06 NO DATA NO DATA NO DATA 2 .17 E- O'S I 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 l 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 JiO 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-65 CU-64 NO 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-05 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 6.05E-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 2.33E-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 SR-91 5.67E-06 NO 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 )J Y-90 9.62E-09 NO DATA 2'.58E-10 NO DATA NO DATA NO DATA 1.02E-04 Y-91m 9.09E-11 NO DATA 3.52E-12 NO DATA NO DATA NO DATA 2.67E-10 Y-91 1.41E-07 NO DATA 3.77E-09 NO DATA NO DATA NO DATA 7.76E-05 Y-92 8.45E-10 NO DATA 2.47E-11 NO DATA NO DATA NO DATA 1.48E-05 Y-93 2.68E-09 NO DATA 7.40E-11 NO DATA NO 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 1.05E-04 NS-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 NO DATA 9.99E-06 TC-99m 2.47E-10 6.98E-10 8.89E-09 NO DATA 1.06E-08 3.42E-10 4.13E-07 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 RU-106 2.75E-06 NO DATA 3.48E-07 NO DATA 5.31E-06 NO DATA 1.78E-04 AG-110m 1.60E-07 1.48E-07 8.79E-08 NO DATA 2.91E-07 NO DATA 6.04E-05 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 8.25E-07 1.73E-06 2.75E-05 NO DATA 2.27E-05 TE-127 1.10E-07 3.95E-08 2.38E-08 8.15E-08 4.40E-07 NO DATA 8.68E-06 TE-129m 1.15E-05 4.29E-06 1.82E-06 3.95E-06 4.80E-05 NO DATA 5.79E-05 TE-129 3.14E-08 1.18E-08 7.65E-09 2.41E-08 1.32E-07 .NO DATA ?.37E-08 TE-131m 1.73E-06 8.46E-07 7.05E-07 1.34E-06 8.57E-06 NO DATA 1.40E-05 TE-131 1.97E-08 8.23E-09 6 *. 2 2 E- 0 9 1.62E-08 8.63E-08 NO DATA 2.79E-09 s
CLINTON.1 2-19 Rev.16-12/97 { _-.
CPS-ODCM TABLE 2.4-3 (cont'd) ADULT INGESTION DOSE FACTORS - DF i (mrem /pCi ingested) ISOTOPE BONE LIVER' T. BODY THYROID KIDNEY LUNG TE-132 2.52E-06 GI-LLI 1.63E-06 1.53E-06 1.80E-06 1.57E-05 NO DATA I-130 7.56E-07 2.23E-06 7.71E-05 - 8.80E-07 1.89E-04 3.48E-06 NO DATA 1.92E-06 I-131 4.16E-06 5.95E-06 3.41E-06 1.95E-03. 1.02E-05 NO DATA I-132 2.03E-07 1.57E-06 5.43E-07 1.90E-07 1.90E-05 0.65E-07 NO DATA 1.02E-07 ~ I-133 1.42E-06 2.47E-06 7.53E-07 3.63E-04 4.31E-06 NO DATA 2.22E-06 I-134 1.06E-07 2.88E-07 1.03E-07 4.99E-06 4.58E-07 NO DATA 2.51E-10 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 1.40E-04 1.21E-04 NO DATA 4.79E-05 1.59E-05 CS-136 2.59E-06 6.51E-06 2.57E-05 1.85E-05 NO DATA 1.43E-05 1.96F-06 2.92E-06 CS-137 7.97E-05 1.09E-04 7.14E-05 NO DATA 3.70E-05 1. 2 M-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-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 3.56E-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 LA-140 2.50E-09 1.2.6E-09 3.33E-10 NO DATA NO DATA NO DATA' 9.2SE-05 LA-142 1.28E-10 5.82E-11 1.45E-11 NO DATA NO DATA NO DATA 4.2SE-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 4.2SE-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 6.45E-11 NO DATA 3.65E-10 NO DATA 2.40E-05 ( , c2.84 x 10-" o*Less than 10-** 1
CPS-ODCM FIGURE 2.5-1 LIQUID RADWASTE TREATMENT SYSTEM CM4DirA
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- Monitors required by Section 2.7 WF01S Floor Drain OWZO1P Chem. Wst. 2WF04T Floor Drain OWE 02PA,B, and C Evaporator Evao. Tank Pump Evaporator Tank Waste Samp. Tk Pumps g WF01S Floor Drain OWE 01FA,B, and C OWZO1T Chem. Waste OWE 01TA and B Evaporator Waste Filters Evaporator Tank Excess Water Tanks OW70lS Chemical OWE 01DA,B, and C IWF04P Fir. Drn. OWE 01PA and B Waste Evaporator Waste Demins Evap. Tank Pump Excess Water Tank Pumps K WF04T Floor Drain OWE 02TA,L, and C 2WF04P Fir. Drn. 1PR036 Service
$ Lv-- ator Tank Waste Sample Tkss Evap. Tank Pump Water PRM OPR040 Liquid RW h Discharge PRM f L y CLINTON-1 2-21 Rev.16-12/97 r _________ _ _ . a n ;t 1
CPS-ODCM FIGURE 2.5-2 SHUTDOWN AND FUEL POOL HEAT EXCHANGER SEPVICE WATER EFFLUENT MONITORS , 1 l SHUTDOWN SHUTDOWN SERY :CE SERVICE RHR HEAT WATER WATER EXCHANGER 'A" _ WEL POOL HEAT / I 3HUTDOWN EXCHANGER SERVICE SHUTDOWN SINK p f SERVICE WATER LOOP <A= MHER SYSTEM SERVICE WATER 1 RI_:-PR004
- Leggs EFFLUENT "A" 1RIX-PR038* /\ \/
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EXCHANGER *B" WATER I l NORMAL C.OOLING-SUPPLY - COMPONFNT COOLING WATER , ZMERGENCY COOLING SUPPLY - SHUTDOWN SERVICE WATER l
*Mo111 tors required by Section ". I 1 PIX-PR038 Shutdown Service 1RIX-PR005 Fuel Pool Heat W3ter Effluent "A" Exchanger Service Water PRM 1RIX-PR039 Shutdown Service- 1RIX-PR004 Fuel Pool Heat Water Effluent "B" Exchanger Service Wa.ter PRM
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CPS-ODCM 2.5 Liquid Radwaste Treatment System 2.5.1 Liquid Radwaste Treatment System - Operation and , Surveillance Requirements j OPERATION REQUIREMENT , The liquid.radwaste treatment system shall be OPERABLE. 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 UNRESTRICTED 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 REQUIREMENT: With radioactive liquid waste being discharged without treatment 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 L days a Spegial Report that includes the following L information: l l 1. Explanation of why liquid radwaste was being ( discharged without treatment, identification of any f ! l inoperable equipment or subsystems, and the reason , I i 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.
SURVEILLANCE REQUIREMENTS 2.5.1.1 Doses due to liquid releases to UNRESTRICTED AREAS shall be projected at least once per 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.
a me o
~
E. l l CPS-ODCM I 2.5.2 Temporary Liquid Radwaste Hold-Up Tanks The use of temporary liquid radwaste hold-up tanks may occur at CPS. To comply with Operational Requirements Manual (ORM) 2.4.4,' the curie limit for liquid radwaste
-) stored in such tanks may be calculated using the methodology presented in Appendix B of NUREG-0133 (BWR-RATAFR code), but limited to less than or equal to 10 curies, excluding tritium.and dissolved or entrained noble gases.
2.6 Doses From Other Significant Liquid Effluent Pathways Section 2.4 of this manual is based upon the aquatic food l and potable water exposure pathways only. Other exposure l pathways, namely shoreline deposits and irrigated crops, may arise at Clinton Power Station and will be included I in the section 2.4 dose contribution if they are likely i to provide a significant contribution to the total dose. ! A pathway is considered significant if a conservative i ' hvaluation yields an additional dose increment greater I l . th.an or equal to 10 percent of the total from all other l existing pathways. Methods for calculating doses from other potentially significant liquid effluent pathways are presented in Appendix A to Regulatory Guide 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. 2.7 Radioactive Liquid Effluent Monitoring Instrumentation 2.7.1 Radioactive Liquid Effluent Monitoring Instrumentation Operation and Surveillance Requirements OPERATION REQUIREMENT The radioactive liquid effluent monitoring instrumentation channels shown in Table 2.7-1 shall be OPERABLE with their alarm / trip setpoints set to ensure that the limits of Section 2.3.1 are not exceeded. The alarm / trip 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 duri.ng releases via the associated pathway. CLINTON.1 2-25 Rev.16-12/97
CPS ,ODCM , REMEDIAL REQUIREMENT:
- a. With a radioactive liquid effluent monitoring instrumentation channel alarm / trip setpoint less !
conservative than required by the above requirement., without delay suspend the release of radioactive - i liquid effluents monitorect by the affected channel, ! or declare the channel inoperable, or change'the l setpoint so it is acceptably conservative.
- b. With less than the minimum number of radioactive liquid effluent monitoring instrumentation channels OPERABLE, comply with the REMEDIAL REQUIREMENT shown
. in Table 2.7-1. Restorc the inoperable instruments i to OPERABLE status within 30 days and, if l
unsuccessful, explain in the next Radioactive l Effluent Release Report why the inoperability was ! not corrected in a timely manner. SURVEILLANCE REQUIREMENTS . 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 and CHANNEL FUNCTIONAL TEST at the frequencies shown in Table 2.7-2. l ( l l O e a
T L NE AM I - DE R 1 22 2 2 333 44 E I MU E RQ E R
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n o ) ) N M a a I NA _ O a ai 111 11 I N NR ( ( s ( ( I AE T 1 1i 1 1 v A HP - T M CO i D N / E 1 M U R T S r - N o I t r G i G o N n on r _ N t I I i D Mo n o _ R n I i o t O o V nt i i 1 T C M O oa t n R a _ I I i i o 7 N T n P td i M O A o aa d 2 M M i T i R a n O t O d R o E T T a N as i L B A N E U L U A D i d R a T U B Rs sc so e t r e a t i d a r e g a _ T F F N s er W R a e o A M cP t E s R o e n S M e A rt c 's i g D R c L Pn i s L I A o A e v e e n U L r tu r c nte i Q A P GEnl e o inn l I NSef S r Lei o L G g e IAuf P uL eo N DELE r Stl S gC E I r ILf e r Enfr Ea . V D a VEfr g e Cef e Crn y I I h OREe n t I uEt I oo l T V c R t a a Vl a Vti n C O s PFra h W EfrW ESt o A R i OeW c Dfe D a O PE D. S t x g Etn el I _ I S RNae E n T ao Gto I D SAe OOWc i NeWi Nas A ret TI i t l Et .t I sI n R ,OLs ITev a o Msea Tn o tea NAcr e o Eacl Aee i IRw ONie H C Rwiu Cdr s N d MI vS Udvc I no i OFa Mr l t Sarr doc v MOR YRen o n ARei NC i
- TESwrore E SC I r D ENd IT ooFon Mditt do VOi V tdt to Let d II u ICntjlip Eunn El c n TTq TI aunenm Tqaa Vca a CAi CTlhouoo Aill Eye ANL RLPP LCR OI IM
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- CPS-ODCM TABLE 2.7-1 (Continued) t' l RADIOACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION j
, TABLE NOTATION i
(a) Channel OPERABILITY shall include the capability of the Main Control Room Central Control Terminal (MCR-CCT) to provide the alarm status of the applicable radiation monitor channel (s) . REMEDIAL REQUIREMENT l REMEDIAL With the number of channels OPERABLE less than REQUIREMENT required by the Minimum Channels OPERABLE 1 requirement, effluent releases may continue via i this pathway provided that prior to initiating a l release: l
., a. At least two independent samples are enalyzed in accordance with Secti'n o 2.3.1.1, and
- b. At least two technically qualified members independently verify the release rate i calculations and discharge line valving: 1 Otherwise, suspend release of radioactive :
effluents via'this pathway. f REMEDI.AL a. With the communication link or the MCR-CCT
, REQUIREMENT inoperable perform CHANNEL CHECK using local 2 monitor indication within 8 hours and at least once per 8 hours thereafter.
- b. With the monitor otherwise inoperable, effluent releases via this pathway may continue provided that at least once per 12 hours, grab samples are collected and analyzed for radioactivity at a Lower Limit of Detection of 5.0 x 10-' pCi/cc for the Principal Gamma Emitters. The Principal Gamma Emitters are: Mn-54, Fe-59, Co-58, Co-60, Zn-65, Mo-99, Cs-134, Cs-137, and Ce-141.
Ce-144 shall be measured with an LLD of
, 5.0 x 10-' pCi/cc. Dissolved and Entrained Gases (gamma emitters only) shall be measured with an LLD of 1.0 x 10-5 pC1/cc. These Dissolved and Entrained Gases are: Xe-133, Xe-135, Xe-138, Kr-85m, Kr-87, and Kr-88.
CPS-ODCM . TABLE 2.7-1 (Continued)_ RADIOACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION ) TABLE NOTATION REMEDIAL With the number of channels OPERABLE less than i REQUIREMENT required by'the Minimum Channels OPERABLE -
. 3 requirement, effluent releases via this pathway may continue provided the flow rate is estimated at least once per 4 hours during actual releases.
Pump performance curves generated in place may be used to estimate flow. All flows diverted from Plant Service Water must be taken into account when estimating dilution flow when Plant Service Water is the only dilution source. REMEDIAL With the number of channels OPERABLE less than REQUIREMENT rpquired by the Minimum Channels OPERABLE 4 ' requirement, liquid additions to this tank may continue provided the tank liquid level is estimated during all liquid additions to the tank. 5
/
CLINTON-1 2-29 Rev.16-12/97
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- CPS-ODCM TABLE 2.7-2 (Continued)
RADIOACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION ' SURVEILLANCE REQUIREMENTS y L TABLE NOTATIONS (1) The CHANNEL FUNCTIONAL TEST shall also demonstrate that automatic icolation of this pathway occurs and that the MCR-CCT provides annunciation and event display in response to each of the following conditions:
- 1. Instrument indicates measured levels above the alarm / trip (HIGH) setpoint.
- 2. Detector failure (LOW EAIL, HI EAIL).
- 3. Sample flow failure (EXTERNAL FAIL) .
- 4. Instrument not set in normal operate mode (UNINITIALIZED, CALIBRATE, MAINTENANCE, or STANDBY.)* i
'(2) The CHANNEL FUNCT. AAL TEST shall also demonstrate that the i MCR-CCT responds with annunciation and event display to each of the following conditions: -
- 1. Instrument indicates measured levele above the alarm f (HIGH) setpoint. '-
- 2. Detector failure (LOW EAIL, " HI EAIL-) .
- 3. Sample flow failure (EXTERNAL FAIL).
- 4. Instrument not set in normal operate mode
,(UNINITIALIZED, CAI;IBRATE, MAINTENANCE, or STANDBY.)*
1 l i l
~
l 1
*A demonstration of automatic isolation of the release pathway is-not applicable to this condition.
CT.TNTAN-1 2-32 Rev .16-17 / 47
~
1 CPS-ODCM TABLE 2.7-2 (Continued) RADIOACTIVE LIOUID EFFLUENT MONITORING INSTRUMENTATION SURVEILLANCE REQUIREMENTS TABLE NOTATIONS (3) The initial CHANNEL CALIBRATION shall be performed using one or more of the reference standards certified by the' National Institute of Standards and Technology (NIST) or using standards that have been obtained from suppliers that participate in measurement assurance activities with NIST. 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 vestifying indication of flow during periods of release. . CHANNEL CHECK shall be made at least once per 24 hours on days which continuous, periodic, j or batch releases.are made. (5) Determine that channel communication is established to the MCR-CCT.
)
e 9 P
,Y CLINTON-1 2-33 Rev.16-12/97
i CPS-ODCM 3.0 GASEOUS EF'FLUENTS 3.1 Introduction t 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 Purge and mechanical vacuum pump ) discharge may be considered short term releases.
]
There are two gaseous effluent release points to the environment: the Common 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 Engi~neered 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 j secondary containment. The Common Station HVAC Stack ("HVAC Stack") receives process and ventilation exhaust from the following inputs:
- 1) Continuous Containment Purge (CCP)
- 2) Containment Building Ventilation
- 3) Turbine Building. Ventilation 4 )- Radwaste Building. Ventilation f
- 5) Auxiliary Building Ventilation '
- 6) Fuel Building Ventilation
- 7) Auxiliary Building Refrigerant Purge
- 8) Laboratory Ventilation System
- 9) Counting / Equipment Decon Rooms Ventilation
- 10) Steam Packing Exhauster
- 11) Mechanical Vacuum Pump
- 12) Drywell Purge The effluen.t 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 HVAC Stack, with the exception of input numbers 7 through 10, can be monitored prior to entering the stacP .
Figure 3.1-1 delineates the CPS site boundary for implementation of gaseous effluent 10CFR20 and 10CFR50, Appendix I Release Rate Limits. cr.T NTnN- 1 3-1 now 1 c-19 /o7
l l
. l t
CPS-ODCM j 3.2~ Gaseous Effluent Release Point Monitoring 3.2.1 HVAC Stack Process Radiation Monitoring (PRM) System y The HVAC Stack inputs are monitored for radioactivity prior to discharge to the environment by the HVAC Stack PRM. The PRM detector configuration provides effluent monitoring using nine (9) channels as follows:
- 1) Beta scintillator for particulates
- 2) Alpha surface barrier detector to account for the radon / thoron contribution to the beta particulate measurement
- 3) Gamma scintillator for iodine
- 4) Iodine backgro.und subtraction
- 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
- 8) Sample pressure indication at the HVAC PRM l 9) Sample flow rate indication at the HVAC PRM This monitor has no control function but annunciates in the Main Control Room where proper response actions will be initiated in accordance with CPS procedures.
3.2.2 SGTS Stack Process Radiation Monitoring (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 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) Beta scintillator for particulates
- 2) Gamma scintillator for iodine I
b l CLINTON-1 3-2 Rev.16-12/97
r CPS-ODCM
- 3) Iodine backgiaund subtraction f
- 4) Beta scintil-lator for low range noble gas !
- 5) )
Energy-compensated G-M detector for intermediate' range' noble ghs
- 6) Energy-compensated G-M detector for gamma area subtraction
- 7) Alpha surface barrier detector to account for the radon / thoron contribution to the beta particulate measurement
- 8) Sample pressure indication at the SGTS PRM
- 9) Sample flow-rate indication at the SGTS PRM i
This monitor has no control function but annuncistes in i the Main Control Room where proper response actions will be initiated in accordance with CPS procedures. 3.3 Main Condenser Off-Gas Monitoring System 3.3.1 Pre-Trea'tment Air Ejector Off-Gas Process Radiation Monitor (PRM) ( l The Pre-Treatment Off-Gas PRM monitors hydrogen ( recombiner effluent for gross noble gas radioactivity. ; t-Th.fs 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-compensated G-M detector mounted in a gas volume. The. monitor has no control function but annunciates in the Main Control Room where proper response actions will be initiated in accordance with CPS procedures. CLINTON-1 3-3 nov 16-1?/o7
CPS-ODCM 3.3.2 Post-Treatment Air Ejector Off-Gas Process Radiation Monitor (PRM) The Post-Treat:aent Off-Gas PRM monitors the gaseous
}
radioactivity at upstream, intermediate or downstream sections of the charcoal adsorber beds prior to the effluent entering the station HVAC Stack for release to the environment (see Figure 3.3-1). The PRM detector configuration is as described for the HVAC Stack PRM (Section 3.2.1) . The monitor has two control functions. Upon detection of noble gas activity in excess of the ALERT setpoint, the 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 isolat'de from the HVAC Stack and a reactor scram may occur if loss of :ondenser vacuum occurs. The Main Condenser Off-Gas Treatment System is shown in Figure 3.3-1, 3.4 10CFR20 Release Rate Limits The Operation and Surveillance Requirements concerning 10CFR20 Release Rate Limits are specified in Section 3.4.1. 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 REQUIREMENT The dose rate due to radioactive materials released in gaseous effluents from the site to areas at and beyond the SITE BOUNDAhY (see Figure 3.1-1) shall be 1.imited to the following:
- a. For noble gases: 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
/
CLINTON-1 3-4 Rev.16-12/97
CPS-ODCM
- b. For iodine-131, for iodine-133, for tritium, and for all radionuclides in particulate form with half lives greater than 8 days: Less than or equal I.
to 1500 mrem /yr to any organ. , j This requirement applies at all times. 1 REMEDIAL REQUIREMENT: , With the dose rate (s) exceeding the above limits, l immediately restore the release rate to within the above limit (s). SURVEILLANCE REQUIREMENTS I l 3.4.1.1 The dose rate due to noble gases in gaseous effluents ' shall be determined to be within the above limits in ! accordance with the methodology and parameters in Section 3.4.2 by obtaining representative samples and , performing analyses in accordance with the sanpling and l l analysis' program specified in Table 3.4-1. l l \ l 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 be determined to be within the above limits in accordance i with the methodology and parameters in Section 3.4.3 by $ obtaining representative. samples and performing { , analyses in accordance with the sampling and analysis program specified in Table 3.4-1. e MT W ..M M. 9 4 M P e G # 4 A FA M
CPS-ODCM d TABLE 3.4-1 i RADIOACTIVE GASEOUS WASTE SAMPLING AND ANALYSIS PROGRAM ) Lower Limit of Detection Sampling Analysis Type of LLD Gnaeous Release Type Frequency Frequency Activity Analysis (pCi/cc) A. Station HVAC Exhaust
- 1. Noble Gas and W* W* Principal Gamma 1.0 x 10-
Tritium Release Grab Emitters
- 1.0 x 10
H-3
- 2. Icdines Release Continuous' W* I-131 1. 0 x 10-12 I-133 1.0 x 10'**
l 3. Particulates Release Continuous 3 W" Principal Ga'ama 1.0 x 10*** l M Emitters
- 1.0 x 10***
Composite Gross Alpha i Activity l Q Sr-89, Sr-90 1.0 x 10*** l Composite Activity D. Standby Gas Treatment System Exhaust, when flow exists l 1. Ntble Gas and W W Principal Gamma 1.0 x 1F Tritium Release Grab Emitters
- 1.0 x 10-
l H-3
- 2. Iodines Release Continuous' W*
- I-131 1.0 x 10~**
I-133 1.0 x 10-*' l
- 3. Particulates Release Continuous' W8 Principal Gamma 1.0 x 10"**
l M Emitters *. 1.0 x 10-** Composite Gross Alpha ! Activity l Q Sr-89,'Sr-90 1.0 x 10~** Composite Activity l i
\
CLINTON-1 3-6 Rev.16-12/97
CPS-ODCM . TABLE 3.4-1 (Continued) , RADIOACTIVE GASEOUS WASTE SAMPLING AND ANALYSIS PROGRAM TABLE NOTATIONS -
'The 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: LLD = 4. 66 sb/ [E x V x 2.22 x 10' x Y x exp " 1. Where: 1 LLD is the "a priori" lower limit of detection as defined I above, as microcuries per unit mass or volume, ! s3 is the standard deviation of the background counting rate I or of the counting rate of a blank sample as appropriate, as counts per minute,s,= Uhu where Rm = background counts t=the background count time * [ ~ l E is the counting efficiency, as counts per disintegration, V is the sample size in units of mass or volume, 2.22 x 10" is the number of disintegrations per minute per' microcurie, Y is the fractional' radiochemical yield, when applicable, A is the radioactive decay constant for the particular radionuclide (seed) and At for plant effluents is the elapsed time between the l midpoint of sample collection and the midpoint of the ! counting interval (sec). '
\
Typical values of E, V, Y, and 6t should be used in the i calculation. I i l l L l CLINTON-1 3-7 Rev .16-12 / 97
C PS-ODCM TABLE 3.4-1 (Continued)
' RADIOACTIVE GASEOUS WASTE SAMPLING AND ANALYSIS PROGRAM TABLE NOTATIONS (Continued)
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 poster iori (after the fact) , limit for a particular measurement. 2 The principal gamma emitters are: 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 Ce-144 in iodine and particulate releases. Other gamma peaks that are identifiable, together with thos'e of the above nuclides, shall be analyzed and reported in the Radioactive Effluent Release Report pursuant to Technical Specification 5.6.3 in the format outlined in Regulatory Guide 1.21, Appendix B, Revision 1, June 1974.
' Sampling 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.
'The ratio of the sample flow rate to the sampled stream flow rate shall be known for the time period covered by each dose or dose rate calculation made in accordance with Sections 3.4.1, 3.5.1 and 3.5.2.
' Samples shall be changed at least once per 7 days and analysis shall be completed within 48 hours'after changing, or after removal from sampler. Sampling shall also be performed at least once per 24 hours for at' least 7 days following each shutdown, startup, or THERMAL POWER change exceeding 15% of RATED THERMAL
~
POWER in 1-hour period and analyses shall be completed within 48 hours of changing. When samples collected for 24 hours or less are analyze'd, 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 I in the primary coolant has increased more than a factor of 3, and (2) the noble gas monitor on the applicable PRM (HVAC or SGTS) shows that effluent activity has increased more than a factor of
- 3. -
\ l . l CLINTON-1 3-8 Rev.16-12/97
CPS-ODCH 3.4.2 Dose Rate-Due to Noble Gases - In order to comply with Section 3.4.1. (a), the dose rate at or beyond the site boundary due to noble gases [- shall be calculated as follows: De = EgKg [ (X/Q) .Qs.) (1)
=
total body dose rate at time of release, mrem / year D, = Eg (Lg+1.1M ) [ (X/Q),Qi ] i (2)
=
skin dose rate at time of release, mrem / year
. - The terms 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 radioiodines (I-131, I-133), particulates with half-lives > 8 days and tritium shall be calculated as follows: Do = epi i3 [ (X/Q),Qi.] (3)
=
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 i emissions for each identified noble gas ! radionuclide i, mrem /yr per pCi/m' ! Li .= The skin dose factor due to beta i emissions for each identified noble gas radionuclide i, mrem /yr per pCi/m' - Mi = The air dose factor due to gamma emissions for each identified noble gas radionuclide i, mrad /yr per pol /m' (1.1 mrem / mrad converts air dose to skin dose) i C@T0ThTO-R M -
CPS-ODCM Py = 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 for 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.
- 05. = The release rate of noble gas radionuclide i in gaseous effluent from mixed-mode release points, pCi/sec Qi, = The release rate of non-noble gas radionuclide i.in gaseous effluent from
- mixed-mode release points, pCi/sec (X/0) = The highest calculated average relative concentration for any area at or beyond the site boundary from mixed-mode releases, 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 3.4.l(b) .
.The factors K i, L,i 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-1 of Regulatory Guide 1.109 after multiplying the values by the conversion 10' pCi/pCi. 10CFR20 organ dose rate calculations are limited to the inhalation pathway only. Section 3.4.l(a) is applicable to the unrestricted area location characterized by the (X/Q), value which results in the i maximum, total body or skin dose commitment. Should the ) total body and skin locations differ, the selected location shall be that which minimizes allowable
- release rates.
I 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.
\
CLINTON-1 3-10 Rev.16-12/97
)
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'm r
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++ +++++++++++ a ,
l F K a eEEEEEEEEEEEEEE p712 7 6 6 514 212 3 4 s a e r t r.16 946515918488
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m e ( s o d e d d e i . t l c m mm m s 1335578 i - u 55789033333331 - n 88888911111114 l T o - - - - - - i d rrrrrreeeee-KKKKKKXXXXXXXA eer e h T N I a L R + C
CPS-ODCM TABLE 3.4-3 INHALATION PATliWAY DOSE RATE FACTORS (CllILD) - Pu (mrem /yr per pCi/m') rRGAN BONE LIVER T. BODY THYROID KIDNEY LUNG 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 9.88E+04 NO DATA NO DATA NO DATA 4.22E+04 CR-51 NO DATA NO DATA 1.54E+02 0.55E+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 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 2.87E+03 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 CO-60 NO DATA 1.31E+04 2.26E+04 NO DATA NO DATA 7.07E+06 9.62E+04 NI-63 8.21E+1)5 4.63E+04 2.80E+04. NO DATA NO DATA 2.75E+05 6.33E+03 NI-65 2.99EiOO 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 EN-65 4.26E+04 1.13E+05 7.03E+04 NO DATA 7.14E+04 9.95E+05 1.63E+04 EH-69 6.70E-02 9.66E-02 8.92E-03 NO DATA 5.85E-02 1.42E+03 1.02E+04 BR-83 NO DATA NO DATA 4.74E+02 NO DATA NO DATA NO DATA LT 3.70E-15**
BR-84 NO DATA NO DATA 5.40E+02 NO DATA NO DATA NO DATA' LT 3.70E-15 BR-85 NO DATA No DATA 2.53E+01 NO DATA NO DATA NO DATA LT 3.70E-15 RB-06 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 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 1R-90 1.01E+08 NO DATA 6.49E+06 NO DATA NO DATA 1.48E+07 3.43E+05 JR-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 2.68E+05 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 1.04E+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 DATA NO DATA 7.44E+04 3.89E+05 l ER-95 1.90E+05 4.18E+04 3.70E+04 NO DATA 5.96E+04 2.23E+06 6.11E+04 EE-97 1.88E+02 2.72E+01 1.60E+01 NO DATA 3.89E+01 1.13E+05 3.51E+05 NB-95 2.35E+04 9.18E+03 6.55E+03 NO DATA 8.62E+03 6.14E+05 3.70E+04 HO-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 0.10E-05 8.51E-05 1.00E-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+00 1.59E+04 9.95E+04 i RU-106 1.36E+05 NO DATA 1.69E+04 NO DATA 1.84E+05 1.43E+07 4.29E+05 , 1 AG-110m 1.69E+04 1.14E+04 9.14E+03 NO DATA 2.12E4 04 5.40E+06 1.00E+05 T"-125m 6.73E+04 2.33E+03 9.14E+02 1.92E+03 NO DATA 4.77E+05 3.30E+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 7.07E+00 1.00E+04 5.62E+04 l _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 1 TE-131m 1.34E+02 5.92E401 5.07E+01 9.77E+01 4.00E+02 2.06E+05 3.00E+05 l _TE-131 2.17E-02 8.44E-03 6.59E-03 1.70E-03 5.88E-02 2.05E403 1.33E+03 l l l CLINTON-1 3-12 Rev.16-12/97 1 : u
-ODCM TABLE 3.4-3 (cont'd)
INHALATION PATHWAY DOSE RATE FACTORS (CHILD) - Po ( tmrem/yr per Ci/m') i M BONR~ LIVER T. BODY THYROID KIDNEY LUNG GI-LLI 6PE
.32 4.81E+02 2.72E+02 2.63E+02 3.18E+02 1.77E+03 3.77E+05 1.38E+05
^
l0 8.18E+03 1.64E+04 8.44E+03 1.85E+06 2.45E+04 NO DATA 5'.11E+03 ll 4.81E+04 4.81E+04 2.73E+04 1.62E+07 7.08E+04 NO DATA 2.84E+03 12 2.12E+03 4.07E+03 1.08E+03 1.94E+05 6.25E+03 NO DATA 3.20E+03 l3 1.66E+04 2.03E+04 7.70E+03 3.85E+06 3.30E+04 NO DATA 5.48E+03 i4 1.17E+03 2.16E+03 9.95E+02 5.07E+04 3.30E+03 NO DATA 9.55E+02 i5 4.92E+03 8.73E+03 4.14E+03 7.92E+05 1.34E+04 NO DATA 4.44E+03 34 6.51E+05 1.01E+06 2.25E+05 NO DATA 3.30E+05 1.21E+05 3.84E+03
.36 6.51E+04 1.71E+05 1.16E+05 NO DATA 9.55E+04 1.45E+04 4.18E+03 37 9.07E+05 8.25E+05 1.28E+05 NO DATA 2.82E+05 1.04E+05 3.62E+03 .38 6.33E+02 8.40E+02 5.55E+02 NO DATA 6.21E+02 6.81E+01 2.70E+02 39 1.84E+00 9.84E-04 5.37E-02 NO DATA 8.62E-04 5.77E+03 5.77E+04 l .40 7.40E404 6.48E+01 4.33E+03 NO DATA 2.11E+01 1.74E+06 1.02E+05 41 1.96E-01 1.09E-04 6.36E-03 NO DATA 9.47E-05 2.92E+03 2.75E+02 .42 5.00E-02 3.60E-05 2.79E-03 NO DATA 2.91E-05 1.64E+03 2.74E+00 .40 6.44E+02 2.25E+02 7.55E+01 NO DATA NO DATA 1.83E+05 2.26E+05 .42 1.30E+00 4.11E-01 1.29E-01 NO DATA NO DATA 8.70E+03 7.59E+04 ,41 3.92E+04 1.95E+04 2.90E+03 NO DATA 8.55E+03 5.44E+05 5.66E+04 43 3.66E+02 1.99E+02 2.88E+01 NO DATA 8.36E+01 1.15E+05 1.27E+05 ,44 6.77E+06 2.12E+06 3.62E+05 NO DATA 1.17E+06 1.20E+07 3.89E+05 ,43 1.85E+04 5.55E+03 9.14E+02 NO DATA 3.00E+03 4.33E+05 9.73E+04 .44 S.96E-02 1.85E-02 3.00E-03 NO DATA 9.77E-03 1.57E+03 1.97E+02 ,47 1.08E+04 8.73E+03 6.81E+02 4.81E+03 NO DATA 3.28E+05 8.21E+04 1.63E+01 9.66E+00 4.33E+00 17
- 39 4.66E+02 3.35E+01 2.35E+01 NO DATA NO DATA NO DATA 9.73E+01 4.11E+04 5.81E+04 9.10E+04 6.40E+04 -
( 12 x 10' ' eco than 3.~10 x 10* l l LTON-)1 . . . . _ _ 3-R3 mem shss#@T
CPS-ODCM TABLE 3.4-4 LOCATION OF MEMBERS OF THE PUBLIC WITHIN THE CPS SITE BOUNDARY AND THEIR ASSOCIATED OCCUPANCY FACTORS
- Distance Occupancy Location (mile / meter) Sector (hrs /yr)
Road 0.3/495 SE 243(1) Agricultural Acreage (2) 0.9/1372 SSW 966(3) Clinton Lake .0.2/335 NW 2208(4) Department of 0.8/1287 ESE 2208(5) Conservation Recreation Area Residence 0.8/1219 SW 8760 Residence 1.5/2414 WSW 8760 Residence 1.7/2736 SSE 8760 (1) Assumes travel on road for forty minutes per day. * (2) Maximum farm acreage (276) within site boundary. (3) Assumes 3.5 hours in field per acre 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.
- Doses for such MEMBERS OF THE PUBLIC are provided in the -
Radioactive Effluent Release Report as given in Section 6.3.2. I I l CLINTON-1 3-14 Rev.16-12/97 ,
CPS-ODCM 3.5 10CFR50, APPENDIX I RELEASE RATE LIMITS ' The Operation and Surveillance Requirements concerning f 10CFR50 (Appendix I) Release Rate Limits are specified i in Sections 3.5.1 and 3.5.2. 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 OPERATION 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) shall be limited to the following: Z-
- a. During any calendar quarter: Less than or equal to 5 mrad for gamma radiation and less than or equal to 10 mrad for beta radiation, and
- b. During any calendar year: Less than or equal to 10 mrad for. gamma radiation and less than or equal to 20 mrad for beta radiation.
This requirement applies at all times. REMEDIAL REQUIREMENT:
- a. With the calculated air dose from radioactive i nobles gases in gaseous effluents exceeding any of !
the above limits, in lieu of a Licensee Event 1 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 darliies 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. 4 Cf.T NTON- 1 4 "' ~ ~ ' ~ ~
CPS-ODCM SURVEILLANCE REQUIREMENTS
~
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 at least once per 31 days. 3.5.2 Iodine-131, lodine-133, Tritium, and Radionuclides in Particulate Form - Operatlon and Surveillance Requirements
. OPERATION REQUIREMENT The dose to a MEMBER OF THE PUBLIC from iodine-131, iodine-133, tritium, and all radionuclides in particulate form with half-lives greater than 8 days in gaseous effluents released tc 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 7.5 mrem to any organ, and
- b. During any calendar year: Less than or equal to 15 mrem to any organ.
This requirement applies at all times. REMEDIAL REQUIREMENT:
- a. With the calculated dose from the release of iodine-131, iodine-133, tritium, and radionuclides in particulate form with half lives greater than 8 days, in gaseous effluents exceeding any of the above limits prepare and submit to the 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 that subsequent releases will be in' compliance with the above .
limits. i CLINTON-1 3-16 Rev.16-12/97 1
I CPS-ODCM . SURVEILLANCE' REQUIREMENTS - 3.5.2.1 Cumulative dose contributiens for the current calendar quarter and current calendar year for iodine-131, ( iodine-133, tritium, and radionuclides in particulate form with half-lives greater than 8 days shall be determined in accordance with the methodology and parameters described in Section 3.5.4 at least once per 31 days. 3.5.3 Noble Gas Air Dose Equations The air dose at or beyond the site boundary due to noble gases released-in gaseous effluent will be l determined using the following equations. 3.5.3.1., During any calendar quarter.or calendar year, for gamma i radiation:
=
Dy 3.17 x 10-'E Mii [ (X/Q).Qi.] (4) ! 3.5.3.2 During any calendar quarter or calendar year, for beta-radiation: Dp = 3.17 x 10-'E Nt i[ (X/Q).Qi,,] (S) .; I where. \ l Mi = The gamma air dose factor for each (.
-identified noble gas radionuclide i, mrad / year per pCi/m3 (Mi values are listed in Table 3.4-2).
Ng = The beta air dose factor for each identified noble gas radionuclide i, mrad / year per pCi/m3 (Ni values are l listed in Table ~3'.4-2). (X/Q). = The highest calculated average relative concentration from mixed-mode release points for areas at or beyond the site . boundary, sec/m'. l Qi,, = The total release of noble gas radionuclide i for long-term releases from mixed-mode release points, pCi. Releases shall be cumulative over the calendar quarter or year, as appropriate.
'CLINTON-1 3-17 Rev.16-12/97
CPS-ODCM 3.17 x 10" = The inverse of the number of seconds in I a year. Section 3.5.1 noble gas dose calculations are evaluated
/ - at the site boundary location where maximum air doses prevail. Should the beta and gamma locations differ, the selected location shall be that which minimizes allowable release rates due to the gamma component.
3.5.4 Radioiodines, Particulates and Tritium Dose Equations The dose to an individual at or beyond the site boundary due to radiciodines (I-131, I-133), tritium and particulates with half-lives > 8 days, will be determined suing the follow equation: for any calendar quarter or calendar year, De = 3.17 x 10"E R,13W,0s, i (6) I where Qi, = The releases o( radionuclide 1 (I-131, I-133, tritium and particulates) for releases from' mixed-mode release points,' pCi. Releases shall be cumulative over the calendar quarter or year, as appropriate. J' (D/Q), = The relative deposition from mixed-mode release points for areas at or beyond the site boundary, ni'. W. = The dispersion parameter for estimating the dose to an individual at a controlling location for mixed-mode releases.
= (X/Q),, sec/m', for the inhalation pathway at the location of the critical receptor.
= (D/0),, nI*, for the food and ground plane pathways at the location of the critical receptor.
3.17 x 10-8 = The inverse of the number of seconds in a year. i). CLINTON-1 3-18 Rev.16-12/97 l l
C PS- ODCM . Ry = The dose factor for each identified . radionuclide i, age group (a) and organ j, m'-mrem / year per pCi/sec or mrem / year per \ pCi/m'. 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 cen:as. 3.5.4.1 Dose Factor For Radionuclide i (R.g3 ) The R.g3 values used to calculate D p in equation (6) are
.~
determined separately for each of the potential exposure pathways, namely:
- Inhalation (I)
- Ground Plane Contamination (G)
- Grass-Cow / Goat-Hilk (C)
- Grass-Cow-Meat (M)
- Vegetation (V)
The R.g3 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 Pathway Factor, R*,u 3 R .g3 = K' (BR) (DFAg) ., mrem / year per pCi/m 3 3 (7) where K' = A units conversion constant, 10' pCi/pCi (BR), = The breathing rate of the receptor age group (a), m'/ year
=
1400 (infant)
=
3700 (child) -
=
8000 (teen and adult) Values for (BR), are obtained from NUREG-0133, pg. 32 1 CLINTON-1 3-19 Rev.16-12/97
CPS-ODCM ( D fag ) . = The organ inhalation dose factor for receptor of age group (a) for radionuclide i, mrem /pCi. Values for (DFA ), were obtained 3
)
from Tables E-7 through E-10 of Regulatory Guide 1.109 and are presented in Tables 3.5-1 through 3.5-4 of this manual. 3.5.4.1.2 Calculation of the Ground Plane Pathway Factor, R" Rg = K'K" (SF) (DFG ) [ (1-e' **) /1 ] , i 3 (8) m -mrem / year per pCi/sec where K' = A units conversion constant, 10' pCi/pCi
.- K" = A units conversion constant, 8~160 hour / year SF = The shielding factor, dimensionless l = 0.~1 as suggested in Table E-15 of Regulatory.
Guide 1.109 DFG 3 = The ground plane dose conversion factor for radionuclide 1, mrem / hour per pCi/m* Values for DFGt were obtained from Table E-6 of Jj Regulatory Guide 1.109 and are presented in Table 3.5-5 of this manual. t l At = The decay constant for radionuclide i, sec* - 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".33 R .33
= K' [Qr (Uap) / ( A + Aw) ] F,(r) (DFL1) . t (9)
[f pf /Y p+ (1-f f.) p e i*h/Y.] e l*f, ' m*-mrem /yr per pCi/sec where K' = A units conversion constant, 10' pCi/pCi CLINTON-1 3-20 Rev.16-12/97
i C PS-ODCri . Or = The cow / goat feed consumption rate, kg(wet)/ day U., = The receptor's milk consumption rate for age r~ group (a), liters / year 1 Yp = The agricultural productivity by unit area of pasture feed grass, kg/m2 Y. = The agricultural productivity by unit area of stored feed, kg/m F. = The stable element transfer coefficient for milk, days / liter r = Fraction of deposited activity retained on feed grass, dimensionless
~
(DFL:) . = The organ ingestion dose factor for radionuclide i and the receptor in age group (a), mrem /pC1. Values for (DEL ) . were i obtained from Tables E-ll through E-14 of Regulatory Guide 1.109 and are presented in Table 3.5-6 through 3.5-9 of this manual. At = The decay constant for radionuclide 1, sec 4 Av = The decay constant for removal of activity"on leaf and plant surfaces by weathering, sec (
= 5.73 x 10" sec4 (corresponding to a 14-day half-life)
= The transport time from pasture to animal, to
, tr milk, to receptor, sec th = The transport time from pasture to harvest, to animal, to receptor, sec fp = Fraction of the year that the cow / goat is on pasture, dimensionless
- f. =
Fraction of the cow / goat feed that is pasture grass while the cow / goat is on pasture, dimensionless The input parameters for calculating R an are listed in Table 3.5-10. i
~
j l CLINTON-1 3-21 Rev .16-12 / 97
l l . CPS-ODCM i Tritium I . I The concentration of tritium in milk is based on its airborne concentration rather than the deposition. C R, = K' K" F.OrU,p (DFL ) . 0.75(0.5/H), mrem /yr per pCi/m' (10) where-K" = A units conversion constant, 10' gm/kg H = The absolute atmospheric humidity
= 8 gm/m' (NUREG-0133, p. 34) j -
0.75 = The fraction of total feed that is water, l . .. dimensionless 2 0.5 = The ratio of the specific activity of the feed grass water to the atmospheric water, dimensionless The other parameters are as defined in the calculation o f R*.t3 Carbon - 14
) 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**O or C**Or. The concentration of carbon-14 in milk is therefore based upon its airborne concentration assuming that the vegetation C**/C ratio is the same as the local atmospheric C**/C ratio.
R*34 = K' K" F.QrU.p (DFLg) , p (0.11/ 0.16) , mrem /yr per pCi/m' (11) where p = Fractional equilibrium ratio, dimensionless .
= Ratio of the total annual C-14 atmospheric release time to the total annual photosynthesis time (4400 hours). not to exceed unity
= 1.0 CLINTON-1 3-22 Rev.16-12/97
CPS-ODCM ' O.11 = Natural carbon fraction of total plant mass, ' dimensionless O.16 = Atmospheric natural carbon concentration, gm/m' t The other parameters are as defined in the calculation of R*r 3.5.4.1.4 Calculation of the Grass-Cow-Meat Pathway Factor, R".g3 R".i3
= ( K' Or. (U.p) / ( At + L) ] Fr (r) (DFL ) .
i l [f pf./Y p+ ( (1-f f.) p /Y.] e i*h) e i's, l m*-mrem /yr per pCi/sec (12) l l where
.' K' = A units conversion constant, 10' pCi/ Ci i
l U.p = The receptor's meat consumption rate for age group (a), kg/ year l Fr = The stable element transfer coefficient, j days /kg l ! t. = The transport time from slaughter of meat L animal to receptor, seconds tn = The transport time from crop field to receptor, seconds (DFLt ) . = The organ ingestion dose factor for radionuclide 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"i3 are listed in Table 3.5-11. All other terms are as defined for equations (9) and (10) . l Tritium . The concentration of tritium in meat is based on its airborne concentration rather than the deposition. R", = K' K" FrQrU.p (DFL ) . [ 0. ~15 (0. 5/H) ) , i mrem /yr per pCi/m 3 (13) CLINTON-1 3-23 Rev.16-12/97
l CPS-ODCM The terms in equation (13) are as defined in equations ! (10) and (12). 3) Carbon - 14 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"O or i C"O2 . The concentration of carbon-14 in meat is ,- therefore based upon its airborne concentration l assuming that the vegetation C"/C ratio is the same as ' the local atmospheric C"/C ratio.
= ;K' K" FrQf U.p(DFL ), p (0.11/0.16) , j R*u i '
! mrem /yr per pCi/m' (14) The terms in equation (14) are as defined in equations l (11) and (13). 3.5.4.1.'5 Calculation of the Vegetation Pathway Factor, R",t3 I R*.33
= K' [ (r) / [Y,(At + L) ) ) (DFL ) .
i [U.fte~Ai 'L + U .f e d i*h), 8 m'-mrem /yr per Ci/sec (15) where
)! K' = A units conversion constant, 10' pCi/pCi U', = The consumption rate of fresh' leafy vegetation by the receptor in age group (a),
kg/ year. , U'. = 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, dimensionless f, = The fraction of the annual intake of stored vegetation grown locally,'dimensionless , to = The average time between harvest of leafy vegetation and its consumption, seconds tw = The average time between harvest of stored vegetation and its consumption, seconds r-
}s CLINTON-1 3-24 Rev.16-12/97
C PS-ODCM. . Y, = the vegetation area density, kg/m' (DFLi ) . = The organ ingestion dose factor for radionuclide 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*.g3 are listed in Table 3.5-12. All other terms are as. defined for equations (9) and (14) . Tritium The concentration of tritium in vegetation is based on its airborne concentration rather than the deposition. RY.r = K ' K" (U**.f t , +sU .f,) (DFL ) . (0.75(0.5/H)], 3
- '- mrem /yr per pCi/m' (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-14 is assumed to be released as an oxide, either C**O or C**Or. The concentration of carbon-14 in vegetation is therefore based upon its airborne concentration assuming that the vegetation C**/C ratio is the same as [ the local atmospheric C**/C ratio. R*i . = K' K" (U*'.ft , + U'.f,) (DFLa) , p (0.11/0.16) , mrem /yr per pCi/m* (17) . The terms in equation (17) are as defined in equations (11) and (15) . The pathway dose rate factors ( R*. t 3 , Rc.i3, R".i3, R".33, R"i ) , by age group are listed in Table 3.5-13 through 3.5-31. 3.6 Gaseous Radwaste (Offgas Treatment) 3.6.1 Gaseous Radwaste (Offgas Treatment) System - Operation and Surveillance Requirements . CLINTON-1 3-25 Rev.16-12/97
CPS-ODCM OPERATION REQUIREMENT l The GASEOUS RADWASTE (OFFGAS) TREATMENT SYSTEM shall be ii in operation. This requirement applies whenever the main condenser steam jet air ejector system is in operation. REMEDIAL REQUIREMENT:
- a. With gaseous radwaste from the main condenser air
, ejector system being discharged without treatment for more than 7 days, 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. 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.
SURVEILLANCE REQUIREMENT 3.6.1.1 The GASEOUS RADWASTE (OFFGAS) TREATMENT SYSTEM shall be' verified to be in operation once every 12 hours when the main condenser air ejector is in use to ensure that the main condenser offgas treatment system is functioning. NOTE When 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 may be calculated to account for the increased fractions of short-lived noble gases. The noble gas release fractions shall be based - either on actual measured values or on design basis noble gas concentration fractions (30-minute delay) in the primary coolant offgas. a' CLINTON-1 3-26 Rev.16-12/97
l CPS-ODCM . 3.7 Ventilation Exhaust Treatment ' 1 3.7.1 Ventilation Exhaust Treatment system - Operation and Surveillance Requirement ,- t OPERATION REOUIREMENT The VENTILATION EXHAUST TREATMENT SYSTEM (VETS) 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 exceed 0.3 mrem to any organ in a 31-day period. This requirement applies at all times other than when the VETS is undergoing routine maintenance. REMEDIAL REQUIREMENT:
- a. With gaseous waste being discharged without treatment and in excess of the above limit, 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. 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.
SURVEILLANCE REQUIREMENTS 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.*
*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 reducing the projected impact'to less than 0.3 mrem, the VETS shall be used.
CLINTON-1 ' 3-27 Rev.16-12/97
CPS-ODCM 3.7.1.2 The installed VENTILATION EXilAUST TREATMENT SYSTEM shall be considered OPERABLE by meeting the Operation Requirements of Sections 3.4, 3.5.1, and 3.5.2. 3.8 Effluent Monitor.Setpoint Calculations Gaseous effluent Process Radiation Monitor (PRM) alarm setpoints shall be calculated to ensure that the instantaneous dose rate in unrestricted areas due to noble gases released do not exceed 500 mrem / year to the total body and 3000 mrem / year to the skin. The initial setpoints were calculated using the BWR/ GALE code radionuclide mix obtained for CPS; when the actual radionuclide mix can be determined, it will be used for setpoint calculations. The PRM setpoints are based on the instantaneous noble gas dose rates and are applied at the point of which the effluent enters an unrestricted area. Due to PRM limitations, non-noble gas setpoints will not be implemented 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 Table 3.4-1. Both total body and skin dose setpoints will be calculated and the more restrictive limit applied to
): the respective PRM. The actual setpoint used may be lower than the restrictive limit since the two release points will be partitioned such that their sum does not exceed 100 percent of the restrictive limit. The !
I percentages used to partition the release points could vary at plant discretion to accommodate plant :'
' operational conditions. In no case will the combined releases due to variations in the PRM setpoints result in effluent limits being exceeded.
3.8.1 Total Body Dose Rate Setpoint 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 relationship: (18) fy. = Cn/ (EgCn) , dimensionless
)'
CLINTON-1 3-28 Rev.16-12/97
C PS-ODCM . wher.e Cy = The measured concentration of identified noble gas radionuclide i in gaseous effluent release path j, pCi/cc ' The maximum acceptable release rate of all noble gases in release path j to comply with Section 3.4.1 is calculated by using the equation: Or3 = 500 F 3/ [ (X/0) 3 E (K F 3)], pCi/sec t i (19) where Ch3
= The maximum acceptable release rate of all noble gases in release path j, pCi/sec F3 = 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 average relative (X/0)3 concentration of release path j at the site i
boundary Ki = The total body dose factor due to gamma emissions of noble gas radionuclida i as listed in Table B-1 of Regulatory Guide 1.109 and Table 3.4-2 of this manual, mrem /yr per pCi/m' fu = The fraction as defined by equation (IS), dimensionless The total maximum acceptable concentration setpoint of noble gas radionuclides in release path j is calculated using the following equation: Cy3 = OT3 /R 3
, pCi/cc (20) where C,3 = The total-maximum acceptable concentration setpoint of all noble gases in release path j, pCi/cc CLINTON-1 3-29 Rev.16-12/97
C PS-ODCM 073
= The maximum acceptable release rate of all noble gases in release path j determined from equation (19), pCi/sec R3 = The effluent release rate of release point j, cc/sec 3.8.2 Skin Dose Rate Setpoint To ensure compliance with the section 3.4.l(a) skin
! dose rate limit,.PEGi setpoints shall be calculated l using the methodology presented in Section 3.8.1 and by i substituting the following equation for equation (19): Oss = 3000F3/ [ (X/Q) 3 E (L +1.1M ai3) ] , pCi/sec i 3 i (21) l where- , i
- 1 Os3
= The maximum acceptable release rate of all noble gases in release path j, pCi/sec F3 = 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 l ** Li = The skin dose factor due to gamma emissions for each identified noble gas radionuclide i, mrem /yr per pCi/m', as listed in Table 3.4-2 of this manual.
1.1 = An air dose to skin dose equivalent conversion factor, mrem / mrad Ms
= The air dose factor due to gamma emissions for each identified noble gas radionuclide i, -
mrad /yr per pCi/m', as listed in Table 3.4-2 of this manual f i3 = The fraction defined by equation (18) l' CLINTON-1 3-30 Rev.16-12/97
i C PS -ODCM The calculated total body and skin maximum acceptable concentration setpoints are compared and the more restrictive setpoint used. A safety factor may also be applied to the concentration setpoint calculated by equation (20) to' compensate for statistical fluctuations and measurement errors. 3.9 Radioactive Gaseous Monitoring Instrumentation 309.1 Offgas Radiation Monitoring Instrumentation - Operation and Surveillance Requirements OPERATION REQUIREMENT The offgas radiation monitoring instrumentation channels shown in Table 3.9.1-1 shall be OPERABLE, with their alarm / trip setpoints within the specified limits. This requirement applies during operation of the main 4' condenser air ejector (s). s 1 REMEDIAL REQUIREMENT: l
- a. With a radiation monitoring instrumentation channel alarm / trip setpoint exceeding the value shown in Table 3.9.1-1, adjust the setpoint to within the limit within 4 hours or declare 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 REQUIREMENTS 3.9.1.1 Each of the above required radiation monitoring instrumentation channels shall be demonstrated OPERABLE by the performance of the CHANNEL CHECK, SOURCE CHECK, CHANNEL FUNCTIONAL TEST and CHANNEL CALIBRATION at the frequencies shown in Table 3.9.1-2. 1
)
CLINTON-1 3-31 Rev.16-12/97
7 9
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lt t N yv s e e T to n y D wD A tbi n eir o S o T non e gvPdci eg l g N eNo m ni nit ttnFn E tm - M t a atratae nai i M y e Rco ans err er U a Atmmia u ul u R T eMt rRi tRrM h gsnat rl foa ma irome l ws ps 1 S tPv P iaol uee fl e ae N
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CPE-ODCM TABLE 3.9.1-1 (Continued) . OFFGAS RADIATION MONITORING INSTRUMENTATION TABLE NOTATIONS a Alarm only. l { b A channel may be placed in an inoperable status for up to 1 hour for the purpose of performing surveillances. Radioactivity concentration expected at the monitor location
" a noble gas mix with a 2.9-minute decay.
d Radioactivity concentration expected at the monitor location is a noble gas mix released from the off-gas treatment system. I e Channel OPERABILITY shall include the capability of the Main Control Room Central Control Terminal (MCR-CCT) to provide the alarm status of the applicable radiation monitor channel (s). REMEDIAL REQUIREMENT REMEDIAL REQUIREMENT a. With the MCR-CCT inoperable, j 5 l
- 1. Perform a CHANNEL CHECK using local monitor indication within 8 hours and at (
least once per 8 hours thereafter, and
- 2. Restore the MCR-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 l Special Report outlining the cause of the CCT failure or malfunction and the action taken to restore the inoperable equipment to OPERABLE status.
4 CLINTON-1 3-33 Rev.16-12/97
CPS-ODCM TABLE 3.9.1-1 (Continued) OFFGAS RADIATION HONITORING INSTRUMENTATION TABLE NOTATIONS
- 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
- 2. The post-treatment air ejector off-gas PRM high range noble gas activity monitor is OPERABLE, or the provisions
. of REMEDIAL REQUIREMENT 6-b are in effect. 1 REMEDIAL REQUIREMENT a. With the MCR-CCT inoperable, 6
- 1. Perform a CHANNEL CHECK using local monitor indication within 8 hours and at s ) least once per 8 hours thereafter, and i
- 2. Restore the MCR-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.
]
CLINTON-1 3-34 Rev 16-12/97
CPS-oncy l TABLE 3.9.1-1 (Continued) l l OFFGAS RADIATION MONITORING INSTRUMENTATION ! i
/
TABLE NOTATIONS (
- b. With the Post-treatment Off-gas PRM High Range Noble Gas Activity Monitor otherwise inoperable, effluent releases via this pathway may, continue provided grab samples.are taken at least once per 8 hours, and a noble gas gamma isotopic analysis performed within 24 hours.
REMEDIAL REQUIREMENT 7 With the number of channels OPERABLE less than required by the minimum channels OPERABLE requirement, effluent releases via this pathway may continue provided the flow rate is estimated at least once per 8 hours. I 4 [
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CPS-ODCM TABLE 3.9.1-2 (Continued) OFFGAS RADIATION MONITORING INSTRUMENTATION SURVEILLANCE REQUIREMENTS ,. 8 TABLE NOTATION a Automatic isolationCALIBRATION. during the CHANNEL of valve IN66-F060 shall be demonstrated (1) The CHANNEL FUNCTIONAL TEST shall also demonstrate that the MCR-CCT responds with annunciation and event display to each of the following conditions:
- 1. Instrument indicates measured levels above the alarm / trip (HIGH) setpoint.
-2,- Detector failure (LOW EAIL, HI EAIL) .
- 3. Sample flow failure (EXTERNAL FAIL).
- 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 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. I CLINTON-1 3-37 Rev.16-12/97
CPS-ODCM 3.9.2 Radioactive Gaseous Effluent Monitoring Instrumentation
- Operation-and Surveillance Requirements g OPERATION REOUIREMENT The radioactive gaseous effluent monitoring instrumentation channels shown in Table 3.9.2-1 shall be OPERABLE with their alarm / trip setpoints set to ensure that the limits of Section 3.4.1 and Technical Specification 3.7.5 are not exceeded. The alarm / trip setpoints of these channels shall be determined and adjusted in accordance with the methodology and parameters in this manual. This requirement applies as shown in Table 3.9.2-1.
REMEDIAL REQUIREMENT:
. , 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 radioactive gaseous effluents monitored by the af fected channel, or declare the channel inoperable.
- b. With less than the minimum number of radioactive gaseous effluent monitoring instrumentation channels OPERABLE, comply with the REMEDIAL
-.) REQUIREMENT specified in Table 3.9.2-1. Restore the inoperable instrumentation to OPERABLE status i
within 30 days and, if unsuccessful, explain in the next Radioactive Effluent Release Report pursuant to Technical Specification 5.6.3 why this inoperability was not corrected in a timely manner. SURVEILLANCE REQUIREMENTS 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 I ( operations at the frequencies shown in Table 3.9.2-2. . l 1) l CLINTON-1 3-30 Rev.16-12/97 1 L- ___ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ . _ _ _ . _ . _ _ _ _ _ _ _ _ _ _ _ . . _ ___...__ _ _ _ ___ ___ _ __ __ _..__.____________________ _ ____
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b l r a a li s V U h o b e S R a o b e S R fr yeI R xN o l - e N o l - fu' ScF T E N p e w r N p e w Es i 0 S e mt o T e mt o a tv N C g e a a l g e a al Ce ner I A g S l F sM nar nr g S l F AM) eDo V H Ro nar nr u aR GP u V He-6 u l g , ao e c ee Ro ao e c ee t1 f n4 n hi t Rt inil c i t pi yt t Rt nilc na5 fi0 o gn wnd r mv bs hi ii t pi 1
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t io oo o a ae du io oo o a ae iR uG a HM LM I P SD na ah HM LM I P SD twP ao0 SsV tai t . . . . . t x . . . . . tl1 GeF S a b c d e SE a b cd e SF( SMO T I
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CPS-ODCM TABLE 3.9.2-1 (Continued) I RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION TABLE NOTATIONS a At all times. b During standby gas treatment system operation. c A channel may be placed in an inoperable status for up to 1 hour for the purpose of performing surveillances. d Channel OPERABILITY shall include the capability of the Main Control Room Central Control Terminal (MCR-CCT) to provide the alarm status of the applicable. radiation monitor channel (s) . e Filter media (particulate collection patch for particulates and. charcoal cartridge for iodines) in place with an 1 i operating sample pump constitutes an iodine / particulate sampler. I REMEDIAL REQUIREMENT i REMEDIAL l REQUIREMENT a. With the communication link OR the MCR-CCT inoperable, perform a CHANNEL CHECK 8 using local monitor indication within 8 hours and at least once per 8 hours 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 hours and analyzed for gross noble gas activity within 24 hours.
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 hours after the channel has been declared inoperable, samples required by Table 3.4-1 are continuously collected with auxiliary sampling equipment. 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 hours.
)
CLINTON-1 3-40 Rev.16-12/97
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CPS-ODCM TABLE 3.9.2-2 (Continued) RADIOACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION g SURVEILLANCE REQUIREMENTS TABLE NOTATIONS a At all times. b During operation of the standby gas treatment system.. (1) The CHANNEL FUNCTIONAL TEST shall also demonstrate that the MCR-CCT responds with annunciation and event display to each of the following conditions:
- 1. Instrumend indicates measured levels above the alarm (HIGH) setpoint.
"2.[ Detector failure (LOW EAIL, HI FAIL).
- 3. Sample flow failure (EXTERNAL EAIL) .
- 4. Instrument not set in normal operate mode (UNINITIALIZED, CALIBRATE, MAINTENANCE, or STANDBY).
I (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 intended range of energy 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. c Per Regulatory Guide 1.21, compare the PRM readings with grab sample results for the noble gas and particulate / iodine channels.' Modify the channel calibrations as necessary to
- ensure monitor readings are related to the concentration or .I release rates of nuclides in the monitored path. d#
I d Not applicable if the activity in the sample stream is not high enough to provide a statistically relevant comparison.
\h
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\ i CLINTON-1 3-42 Rev.16-12/97
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CPS-ODCM FIGURE 3.3-1 MAIN CONDENSER OFF-GAS TREATMENT SYSTEM !i
*tMX PR03) , /-
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IN64Z4D)A
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- c*"*" Ef8x LQ)DIA MAD 4 CONDDCEA -M-M FMMAltY/ SECONDARY
, j CONTA!HMDIT DotAUST sots oou uSY TAcx
- Monitors required by Sections 3.9.1 and 3.9.2 ICD 01A Main OCA01TA CV IN66B010B IN66D013 1RIX-PR035 Condenser Separator Tank. Cooler Charcoal Off-Gas Post A Condenser B Adsorber Treatment PRM 1CA01AA Steam OCA01TB CV 1N66Z003A IN66D016 HEPA 1RIX-PR041 Jat Air Separator Tank Dessicant Filter Off-Gas Post Ejector A B Dryer A Treatment PRM 1CA01AB Steam IN66D005A IN66Z003B ORIX-PR001 ORIX-PR003 .
Jat Air Recombiner A Dessicant HVAC Stack PRM Standby Gas Ejector B Dryer B R1 Treatment PRM OCA01PA IN66D005B IN66B011 Gas ORIX-PR002 ORIX-PR004 Condenser Recombiner B Cooler HVAC Stack PRM Standby Gas Vccuum (CV) N2 Trea'tment PRM Pump A OCA01PB CV IN66B010A IN66D012 1RIX-PR034 Pump B Cooler Charcoal off-Gas Condenser A Adsorber Pretreatment i PRM CLINTON-1 3-44 Rev.16-12/97
l l CPS-ODCM TABLE 3.5-1 INHALATION DOSE FACTORS FOR INFANT - (DFAi ) ,
) (mrem per pCi inhaled)
A (UCLIDE BONE LIVER k T. BODY THYROID KIDNEY LUNG GI-LLI 1-3 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 (A-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 0.03E-05 5.53E-05 NO DATA NO DATA NO DATA 1.15E-05 CR-51 NO DATA NO DATA 6.39E-08 4.11E-00 9.45E-09 9.17E-06 2.55E-07 4N-54 NO DATA 1.81E-05 3.56E-06 NO DATA 3.56E-06 7.14E-04 5.04E-06 4N-56 NO DATA 1.10E-09 ,1.58E-10 NO DATA 7.86E-10 8.95E-06 5.12E-05 FE-55 1.41E-05 8.39E-06 2.30E-06 NO DATA NO DATA 6.21E-05 7.82E-07 PE-59 9.69E-06 1.68E-05 6.77E-06 NO DATA NO DATA 7.25E-04 1.77E-05 00-58 NO DATA 8.71E-07 1.30E-06 NO DATA NO DATA 5.55E-04 7.95E-06 20-60 NO DATA 5.73E-06 8.41E-06 NO DATA NO DATA 3.22E-03 2.20E-05 (I-63 2.42E-04 1.46E-05 8.29E-06 NO DATA NO DATA 1.49E-04 1.73E-06 (I-65 1.71E-09 2.03E-10 8.79E-11 NO DATA NO DATA 5.00E-06 3.58E-05 U-64 NO DATA 1.34E-09 5.53E-10 NO DATA 2.84E-09 6.64E-06 1.07E-05 LN-65 1.38E-05 4.47E-05 2.22E-05 NO DATA 2.32E-05 4.62E-04 3.67E-05 EN-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-8 6 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-89 NO DATA 2.29E-07 1.47E-07 NO DATA NO DATA NO DATA 4.87E-08 BR-89 2.84E-04 NO DATA 8.15E-06 NO DATA NO DATA 1.45E-03 4.57E-05 5R-90 2.92E-02 NO DATA 1.85E-03 NO DATA NO DATA 6.03E-03 9.36E-05 7-91 6.83E-08 NO DATA 2.47E-09 NO DATA NO DATA 3.76E-05 5.24E-05 A-92 7.50E-09 NO DATA 2.79E-10 NO DATA NO DATA 1.70E-05 1.00E-04 , r-90 2.35E-06 NO DATA 6.30E-08 'NO DATA NO DATA 1.92E-04 7.43E-05 ! r-91m 2.91E-10 NO DATA 9.90E-12 NO DATA NO DATA 1.99E-06 1.68E-06 r-91 4.20E-04 NO DATA 1.12E-05 NO DATA NO DATA 1.75E-03 5.02E-05 r-92 1.17E-08 NO DATA 3.29E-10 NO DATA NO DATA 1.75E-05 9.04E-05 r-93 1.07E-07 NO DATA 2.91E-09 NO DATA NO DATA 5.46E-05 1.19E-04 ER-95 8.24E-05 1.99E-05 1.45E-05 NO DATA 2.22E-05 1.25E-03 1.55E-05 ER-97 1.07E-07 1.83E-08 8.36E-09 NO DATA 1.85E-08 7.88E-05 1.00E-04 (B-95 1.12E-05 4.59E-06 2.70E-06 NO DATA 3.37E-06 3.42E-04 9.05E-06 40-99 NO DATA 1.18E-07 2.31E-08 NO DATA 1.89E-07 9.63E-05 3.48E-05 PC-99m 9.90E-13 2.06E-12 2.66E-11 NO DATA 2.22E-11 5.79E-07 1.45E-06 PC-101 4.65E-14 5.88E-14 5.80E-13 NO DATA 6.99E-13 4.17E-07 6.03E-07 RU-103 1.44E-06 NO DATA 4.85E-07 NO DATA 3.03E-06 3.94E-04 1.15E-05 RU-105 0.74E-10 NO DATA 2.93E-10 NO DATA 6.42E-10 1.12E-05 3.46E-05 RU-106 6.20E-05 NO DATA 7.7E-06 FO DATA 7.61E-05 8.26E-03 1.17E-04 AG-110m 7.13E-06 5.16E-06 3.57E-06 NO DATA 7.80E-06 2.62E-03 2.36E-05 FE-125m 3.40E-06 1.42E-06 4.70E-07 1.16E-06 NO DATA 3.19E-04 9.22E-06 , TE-127m 1.19E-05 4.93E-06 1.48E-06 3.48E-06 2.68E-05 9.37E-04 1.95E-05 E-127 1.59E-09 6.81E-10 3.49E-10 1.32E-09 3.47E-09 7.39E-06 1.74E-05 PE-129m 1.01E-05 4.35E-06 1.59E-06 3.91E-06 2.27E-05 1.20E-03 4.93E-05 PE-129 5.63E-11 2.48E-11 1.34E-11 4.82E-11 1.25E-10 2.14E-06 1.88E-05 PE-131m 7.62E-08 3.93E-08 2.59E-08 6.38E-08 1.89E-07 1. 4 2E. '04 8.51E-05 kE-131 1.24E-11 5.87E-12 3.57E-12 1.13E-11 2.85E-11 1.47E-06 5.87E-06 i LINTON-1 3-45 Rev.16-12/97
CPS-ODCM TABLE 3.5-1 (continued)_ INHALATION DOSE FACTORS FOR INFANT - ( DFAs ) , (mrem per pCi inhaled) NUCLIDE BONE' LIVER T. BODY- THYROID KIDNEY LUNG GI-LLI TE-132 2.66E-07 1.69E-07 1.26E-07 1.99E-07 7.39E-07 2.43E-04 3.15E-05 I-130 4.54E-06 9.91E-06 3.98E-06 1.14E-03 1.09E-05 NO DATA 1.42E-06
- I-131 2.71E-05 3.1*lE-05 1.40E-05 1.06E-02 3.70E-05 NO DATA 7.56E-07 I-132 1.21E-06 2.53E-06 8.99E-07 1.21E-04 2.82E-06 NO DATA 1.36E-06
- I-133 9.46E-06 1.37E-05 4.00E-06 2.54E-03 1.60E-05 NO DATA 1.54E-06 I-134 6.58E-07 1.34E-06 4.75E-07 3.18E-05 1.49E-06 NO DATA 9.21E-07 1-135 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. 32 E-05 NO DATA 1.36E-04 5.69E-05 9.53E-07 C4-136 3.45E-05 9.61E-05 3.78E-05 NO DATA 4.03E-05 8.40E-06 1.02E-06 CS-137 3.92E 4.37E-04 3.25E-05 NO DATA 1.23E-04 5.09E-05 9.53E-07
*CJ-138 3.61E-07 5.58E-07 2.84E-07 NO DATA 2.93E-07 4.67E-08 6.26E-07 BA-139 1.06E-09 7.035-13 3.07E-11 NO DATA 4.23E-13 4.25E-06 3.64E-05 BA-140 4.0GE-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 LA-140 3. 61Ec07 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 CE-141 1.98E-05 1.19E-05 1.42E-06 NO DATA 3.*l5E-06 3.69E-04 1.54E-05 CE-143 2.09E-07 1.38E-07 1.58E-08 HO DATA 4.03E-08 8.30E-05 3.55E-05 CE-144 2.285-03 8.65E-04 1.263-04 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 U-187 9.26E-09 6.44E-09 2.23E-09 NO DATA NO DATA 2.83E-05 2.54E-05
'P-239 2.65E-07 2.37E-08 1.34E-08 NO DATA 4.73E-08 4.25E-05 1.78E-05
)*1.89x10~
**Less than 10-
CLINTON-1 3-46 Rev.16-12/97
CPS-oocM 4 TABLE 3.5-2 INHALATION DOSE FACTORS FOR CHILD - (DFAs ) . (mrem per pCi inhaled) NUCLIDE BONE' LIVER T. BODY THYROID KIDNEY LUNG GI-LLI H-3 NO DATA 3.04E-07 3.04E-07 3.04E-07 3.04E-07 3.04E-07 3.04E-07 C-14 9.07E-06* 1.82E-06 1.82E-06 1.82E-06 1.82E-06 1.82E-06 NA-24 4.35E-06 4.35E-06 1.82E-06 4.35E-06 4.355-06 4.35E-06 4.35E-06 4.35E-06 J-32 7.04E-04 3.09E-05 2.67E-05 NO DATA NO DATA CR-51 NO DATA .1.14E-05 NO DATA NO DATA 4.17E-08 2.31E-08 6.57E-09 4.59E-06 2.93E-07 pel-54 NO DATA 1.16E-05 2.57E-06 NO DATA 2.71E-06 4.26E-04 6.19E-06 IMN-56 NO DATA 4.48E-10 8.43E-11 NO DATA 4.52E-10 3.55E-06 3.33E-05 p.-55 1.28E-05 6.80E-06 2.10E-06 NO DATA NO DATA 3.00E-05 7.75E-07 FE 5.59E-06 9.04E-06 4.51E-06 NO DATA NO DATA' 3.43E-04 1.91E-05 q C0-58 NO DATA 4.79E-07 8.55E-07 NO DATA NO DATA 2.99E-04 9.29E-06 00 No MTA 3.55E-06 6.12E-06 NO DATA 1.91E-03 NI-63 2.22E-04 NO. DATA 2.60E-05 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 i CU-64 2.27E-05 NO DATA 5.39E-10 2.90E-10 'NO DATA 1.63E-09 2.59E-06 9.92E-06~ F.N-65 1.15E.-05 3.06E-05 1.90E-05 NO MTA - 1.93E-05 2.69E-04 4.41E-06 EN-69 1.81E-11 2.61E-11 2.41E-12 NO MTA 1.58E-11 3.84E-07 DR-83 NO DATA 2.75E-06 NO DATA' 1.28E-07 NO DATA NO DATA NO DATA LT E-24** M-84 NO MTA NO DATA 1.48E-07 NO MTA NO DATA NO DATA LT E-24 i DR-85 ; NO DATA NO DATA 6.84E-09 NO DATA NO DATA NO DATA LT E-24 RB-86 NO DATA 5.36E-05 3.09E-05 NO DATA NO DATA NO DATA 2.16E-06 RB-88 NO MTA 1.525-07 9.90E-08 NO DATA NO DATA NO MTA 4. 66E-0'9 pts-89 NO MTA 9.33E-08 7.83E-08 NO DATA NO DATA NO DATA 5.11E-10 BR-89 1.62E-04 No DATA 4.66E-06 NO DATA NO DATA 5.83E-04 4.52E-05 $R-90 2.73E-02 No MTA . 1.74E-03 NO MTA NO DATA 3.99E-03 9.28E-05 'jt-91 3.28E-08 NO DATA 1.24E-09 NO DATA NO DATA 1.44E-05 4.70E-05 A-92 3.54E-09 NO DATA 1.42E-10 NO DATA NO DATA 6.49E-06 6.55E-05 t-90 1.11E-06 NO DATA 2.99E-08 NO DATA NO DATA 7.07E-05 f 7.24E-05 \ Y-91m 1.37E-10 NO DATA 4.98E-12 NO DATA NO DATA 7.60E-07 4.64E-07 7-91 2.47E-04 NO DATA 6.59E-06 NO DATA NO DATA 7.10E-04 4.97E-05 X-92 5.50E-09 NO DATA 1.57E-10 NO DATA NO DATA 6.46E-06 6.46E-05 K-93 5.04E-08 NO DATA 1.38E-09 NO DATA NO DATA 2.01E-05 1.05E-04 f.R-95 5.13E-05 1.13E-05 1.00E-05 NO DATA 1.61E-05 6.03E-04 1.65E-05 F.R-97 5.07E-08 7.34E-09 4.32E-09 NO DATA 1.05E-08 3.06E-05 9.49E-05 IfD-95 6.35E-06 2.48E-06 1.77E-06 NO DATA 2.33E-06 1.66E-04 1.00E-05 W-99 NO DATA 4.66E-08 1.15E-08 NO DATA 1.06E-07 3.66E-05 3.42E-05 FC-99m 4.81E-13 9.41E-13 1.56E-11 NO DATA 1.37E-11 2.57E 1.30E-06 IC-101 2.19E-14 2.30E-14 2.91E-13 MO DATA 3.92E-13 1.58E-07 4.41E-09 14U-103 7.55E-07 NO DATA 2.90E-07 NO DATA 1.90E-06 1.79E-04 1.21E-05 ptU-105 4.13E-10 NO DATA 1.50E-10 NO DATA 3.63E-10 4.30E-06 2.69E-05 14U-106 3.68E-05 NO DATA 4.57E-06 NO DATA 4.97E-05 3.87E-03 1.16E-04 Mi-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 . PE-127m 6.72E-06 2.31E-06 8.18E-07 1.64E-06 1.72E-05 4.00E-04 1.93E-05 PE-127 7.49E-10 2.57E-10 1.65E-10 5.30E-10 1.91E-09 2.71E-06 1.52E-05 PE-129m- 5.19E-06 1.85E-06 8.22E-07 1.71E-06 1.36E-05 4.76E-04 4.91E-05 FE-129 2.64E-11 -9.45E-12 6.44E-12 1.93E-11 6.94E-11 7.93E-07 6.89E-06 2E-131m 3.63E-08 1.60E-08 1.37E-08 2.64E-08 1.08E-07 5.56Ef05 8.32E-05 /E-131 5.87E-12 2.28E-12 1.78E-12 4.59E-12 1.59E-11 5.55E-07 3.60E-07 i L fLINTON-1 3-47 Rev.16-12/97 l-
CPS-ODCM TABLE 3.5-2 (continued) INHALATION DOSE FACTORS FOR CHILD - (DFA ) . i
;- (mrem per pCi inhaled)
LIVER T. BODY THYROID KIDNEY LUNG GI-LLI NUCLIDE BONE 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
. 1-132 5.72E-07 1.10E-06 5.07E-07 5.23E-05 1.69E-06 NO DATA 8.65E-07 4.48E-06 5.49E-06 2.0BE-06 1.04E-03 9.13E-06 NO DATA 1.48E-06 I-133 2.58E-07 I-134 3.17E-07 5.84E-07 2.69E-07 1.37E-05 8.92E-07 NO DATA I-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 B.93E-05 3.27E-05 1.04E-06 CS-136 1.76E-05 4.62E-05 '3.14E-05 NO DATA 2.58E-05 3.93E-06 1.13E-06 CS-137 2.45E-04 2.23E-04 3.47E-05 NO DATA 7.63E-05 2.81E-05 9.78E-07 CS-138 1."J 1E-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 IA-142 3.50E-10 1.11E-10 3.49E-11 NO DATA NO DATA 2.35E-06 2.05E-05 CE-141 1.06E-05 5.28E-06 7.83E-07 NO DATA 2.31E-06 1.47E-04 1.53E-05 CE-143 9.89E-08 5.37E-08 7.77E-09 NO DATA 2.26E-0a 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 PR-143 4.99E-06 1.50E-06 2.47E-07 NO DATA 8.11E-07 1.17E-04 2.63E-05 PR-144 1.61E-11 4.99E-12 8.10E-13 NO DATA 2.64E-12 4.23E-07 5.32E-08 ND-147 2.92E-06 2.36E-06 1.84E-07 NO DATA 1.30E-06 8.87E-05 2.22E-05 4.41E-09 2.61E-09 1.17E-09 NO DATA NO DATA 1.11E-05 2.46E-05 t0-187 1.26E-07 9.04E-09 6.35E-09 NO DATA 2.63E-08 1.57E-05 1.73E-05 s'P-239
') 2
- 9. 7 0 x 10 '"
9
**Less than 10-"
lh '
)
CLINTON-1 3-48 Rev.16-12/97
1 1 pPS-ODCM ' ) TABLE 3.S-3 INHA1ATION DOSE FACTORS FOR TEEN - ( DFA ) , 3 (mrem per pCd inhaled) 51/CLIDE BONE' LIVER T. BODY THYRO 1D KIDNEY LUNG GI-LLI H-3 NO DATA 1.59E-07 1.59E-07 1.59E-07 1.59E-07 1.59E-07 1. 59 E-07 $-14 3.25E-06* 6.09E-07 6.09E-07 6.09E-07 6.09E-07 6.09E-07 6.09E-07 4A-24 1.72E-06 1. 72 E-06 1.72E-06 1.72E-06 1.72E-06 1.72E-06 P-32 1.72E-06 2.36E-04 1.37E-05 8.95E-06 NO DATA NO DATA NO DATA 1.16E-05 sR-51 NO DATA NO DATA 1.69E-08 9.37E-09 3.04E-09 2.62E-06 3.75E-07 Z-54 NO DATA 6.39E-06 1.05E-06 NO DATA 1.59E-06 2.40E-04 $~56 8.35E-06 NO DATA 2.12E-10 3.15E-11 NO DATA 2.24E-10 1.90E-06 Ji2-55 4.18E-06 2.98E-06 7.18E-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
- O-58 2.23E-05 HO DATA 2.59E-07 3.47E-07 NO DATA NO DATA 1.68E-04 1.19E-05 00-60 NO DATA 1.89E-06 2.48E-06 NO DATA NO DATA 1.09E-03 3 -63 7.25E-05 3.24E-05 5.43E-06 2.47E-06 NO DATA NO DATA 3.84E-05 1.77E-06 bl-65 2.73E-10 3.66E-11 1.59E-11 NO DATA NO DATA 1.17E-06 4.59 E-06 E-64 NO DATA 2.54E-10 1.06E-10 NO DATA 8.01E-10 1.39E-06 7.68E-06 E-65 4 . 82 E.-0 6 1.67E-05 7.80E-06 NO DATA 1.08E-05 1.55E-04 5.83E-06 O-69 6.04E-12 1.15E-11 0.07E-13 NO DATA 7.53E-12 1.98E-07 3.56E-08 ER-83 NO DATA NO DATA 4.30E-08 NO DATA NO DATA NO DATA B 84 LT E-24**
NO DATA NO DATA 5.41E-08 NO DATA NO DATA NO DATA LT E-24 3R-85 NO DATA NO DATA 2.29E-09 NO DATA NO DATA NO DATA LT E-24 E-86 NO DATA 2.38E-05' 1.05E-05 NO DATA NO DATA NO DATA 2.21E-06 1B-88 NO DATA 6.82E-08 3.40E-08 NO DATA NO DATA 1B-89 NO DATA 3.65E-15 NO DATA 4.40E-08 2.91E-08 NO DATA NO DATA NO DATA 4.22E-17 JR-89 5.43E-05 NO DATA 1.56E-06 NO DATA NO DATA 3.02E-04 4.64E-05 JR-90 1.35E-02 NO DATA 8.35E-04 NO DATA NO DATA 2.06E-03 9.56E-05 $-91 1.10E-08 NO DATA 4.39E-10 NO DATA NO DATA 7.59E-06 3.24E-05 A-92 1.19E-09 NO DATA 5.00E-11 NO DATA NO DATA 3.43E-06 1.49E-05 7-90 3.73E-07 NO DATA 1.00E-08 NO DATA NO DATA ( 3.66E-05 6.99E-05 I (-91m 4.63E-11 NO DATA 1.77E-12 NO DATA NO DATA 4.00E-07 3.77E-09 7-91 8.26E-05 NO DATA 2.21E-06 NO DATA NO DATA 3.67E-04 5.11E-05 7-92 1.84E-09 NO DATA 5.36E-11 NO DATA NO DATA 3.35E-06 2.06E-05 i-93 1.69E-08 NO DATA 4.65E-10 NO DATA NO DATA 1.04E-05 7.24E-05 !R-95 1.82E-05 5.73E-06 3.94E-06 NO DATA 8.42E-06 3.36E-04 1.86E-05 !R-97 1.72E-08 3.40E-09 1.57E-09 NO DATA 5.15E-09 1.62E-05 7.88E-05 L-95 2.32E-06 1.29E-06 7.00E-07 NO DATA 1.25E-06 9.39E-05 1.21E-05 10-99 NO DATA 2.11E-08 4.03E-09 NO DATA 5.14E-08 1.92E-05 3.36E-05 E-99m 1.73E-13 4.83E-13 6.24E-12 NO DATA 7.20E-12 1.44E-07 7.66E-07 6-101 7.40E-15 1.05E-14 1.03E-13 NO DATA 1.90E-13 8.34E-08 1.09E-16 E-103 2.63E-07 NO DA'I A 1.12E-07 NO DATA 9. 29 E-07 9.79E-05 1.36E-05 E-105 1.40E-10 NO DA"A 5.42E-11 NO DATA 1.'/6E-10 2.27E-06 1.13E-05 10-106 1.23E-05 NO DATA 1.55E-06 NO DATA 2.38E-05 2.01E-03 1.20E-04 2-110m 1.73E-06 1.64E-00 9.99E-07 NO DATA 3.13E-06 8.44E-04 3.41E-05 G-125m 6.10E-07 2.00E-07 8.34E-08 1.75E-07 NO DATA 6.70E-05 9.38E-06 - U-127m 2.25E-Ob 1.02E-06 2.73E-07 5.48E-07 0.17E-06 2.07E-04 1.99E-05 G-127 2.51E-10 1.14E-10 5.52E-11 1.77E-10 9.10E-10 1.40E-06 1.01E-05 GH129m 1.74E-06 8.23E-07 2.81E-07 5.72E-07 6.49E-06 2.47E-04 5.06E-05 G-129 8.87E-12 4.22E-12 2.20E-12 6.4BE-12 3.32E-11 4.12E-07 2.02E-07 G-131m 1.23E-08 7.51E-09 5.03E-09 9.06E-09 5.49E-08
- 2. 97 E-05 7.76E-05 G-131 1.97E-12 1.04E-12 6.30E-13 1.55E-12 7.72C-12 2.92E-07 1.89E-09 i
LINTON-1 3-49 Rev.16-12/97
I CPS-ODCM TABLE 3.5-3 (continued) INHALATION DOSE FACTORS FOR TEEN - (DFAs ) . (mrem per pCi inhaled) LIVER T. BODY THYROID KIDNEY LUNG GI-LLI HUCLIDE BONE 4.50E-08 3.63E-08 2.74E-08 3.07E-08 2.44E-07 5.61E-05 5.79E-05 TE-132 I-130 7.80E-07 2.24E-06 8.96E-07 1.86E-04 3.44E-06 NO DATA 1.14E-06 4.43E-06 6.14E-06 3.30E-06 1.83E-03 1.05E-05 NO DATA 8.11E-07 I-131 1.99E-07 5.47E-07 1.97E-07 1.89E-05 8.65E-07 NO DATA 1.59E-07
. I-132 ~.29E-06 I-133 1. 52 E-06 2.56E-06 7.78E-07 3.65E-04 4.49E-06 NO DATA 1 1.11E-07 2.90E-07 1.05E-07 4.94E-06 4.58E-07 NO DATA 2.55E-09 I-134 4.62E-07 1.18E-06 4.36E-07 7.76E-05 1.86E-06 NO DATA 8.69E-07 I-135 1.83E-05 1.22E-06 CS-134 6.28E-05 1.41E-04 6.86E-05 NO DATA 4.69E-05 6.44E-06 2.42E-05 1.71E-05 NO DATA 1.38E-05 2.22E-06 1.36E-06 CS-136 8.38E-05 1.06E-04 3.89E-05 NO DATA 3.80E-05 1.51E-05 1.06E-06 CS-137 3.38E-11 C3-138 5.82E-08 1.07E-07 5.58E-08 NO DATA 8.28E-08 9.84E-09 1.67E-10 1.18E-13 4.87E-12 NO DATA 1.11E-13 8.08E-07 8.06E-07 BA-139 l BA-140 6.84E-06 8.38E-09. 4.40E-07 NO DATA 2.85E-09 2.54E-04 2.86E-05
! RA-141 1.'18 E-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 5.99E-08 2.95E-08 7.82E-09 NO DATA NO DATA 2.68E-05 6 09E-05 LA-140 1. 2"*E-06 1.50E-06 LA-142 1.20E-10 5.31E-11 1.32E-11 NO DATA No DATA 3.55E-06 2.37E-06 2.71E-07 NO DATA 1.11E-06 7.61E-05 1.58E-05 CE-141 3.32E-08 2.42E-08 2.70E-09 No DATA 1. 08E-08 1.63E-05 3.19E-05 CE-143 1.08E-04 CE-144 6.11E-04 2.53E-04 3.28E-05 NO DATA 1.51E-04 1.67E-03 1.67E-06 6.64E-07 8.28E-08 NO DATA 3.86E-07 6.04E-05 2.67E-05 PR-143 PR-144 5.37E-12 2.20E-12 2.72E-13 NO DATA 1.26E-12 2.19E-07 2.94E-14 9.83E-07 1.07E-06 6.41E-08 NO DATA 6.28E-07 4.655-05 2.28E-05 ND-147 2.21E-05 W-187 1.50E-09 1.22E-09 4.29E-10 NO DATA NO DATA 5.92E-06 O 4.23E-08 3.99E-09 2.21E-09 NO DATA 1.25E-08 8.11E-06 1.65E-05
))P-239
*3.52 x 10"
**Less than 10~#'
- ')
CLINTON-1 3-50 Rev.16-12/97
- PS-ODCM ,
TABLE 3.5-4 INHALATION DOSE FACTORS FOR ADULT - (DFA ) . (mrem per pCi inhaled) IUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI l- 3 NO DATA 1.5BE-07 1.58E-07 1.58E-07 1.5BE-07 1.58E-07 1.58E-07
- -14 2.27E-06* 4.26E-07 4.26E-07 4.26E-07 4.26E-07 4.26E-07 4.26E-07 IA-24 1.20E-06 1.20E-06 1.28E-06 1.28E-06 1.20E-06 1.28E-06 1.28E-06
- -32 1.65E-04 9.64E-06 6.26E-06 NO DATA NO DATA NO DATA 1.08E-05 lR-51 NO DATA NO DATA 1.25E-08 7.44E-09 2.85E-09 1.80E-06 4.15E-07 01-54 NO DATA 4.95E-06 7.87E-07 NO DATA 1.23E-06 1.75E-04 9.67E-06 04-56 NO DATA 1.55E-10 2.29E-11 NO DATA 1.63E-10 1.18E-06 2.53E-06 PE-55 3.07E-06 2.12E-06 4.93E-07 NO DATA NO DATA 9.01E-06 7.54E-07 PE-59 1.47E-06 3.47E-06 1.32E-06 NO DATA NO DATA 1.27E-04 2.35E-05 0-58 NO DATA 1.98E-07 2.59E-07 NO DATA NO DATA 1.16E-04 1.33E-05 0-60 NO DATA ~1.44E-06 1.85E-06 NO DATA NO DATA 7.46E-04 3.56E-05 II-63 5.40E-05 3.93E-06 1.81E-06 NO DATA NO DATA 2.23E-05 1.67E-06 II-65 1.92E-10 2.62E-11 1.14E-11 NO DATA NO DATA 7.00E-07 1.54E-06
- U-64 NO DATA 1.83E-10 7.69E-11 NO DATA 5.78E-10 0.48E-07 6.12E-06 LN-65 4.05E-06 1.29E-05 5.82E-06 NO DATA 8.62E-06 1.08E-04 6.6CE-06 LN-69 4.23E-12 8.14E-12 5.65E-13 NO DATA 5.27E-12 1.15E-07 2.04E09 BR-83 NO DATA NO DATA 3.01E-08 NO DATA NO DATA NO DATA 2.90E-08 BR-84 NO DATA NO DATA 3.91E-08 NO DATA NO DATA NO DATA 2.05E-13 BR-85 NO DATA NO DATA 1.60E-09 NO DATA NO DATA NO DATA LT E-24**;
W-86 NO DATA 1.69E-05 7.37E-06 NO DATA NO DATA NO DATA 2.08E-06 W-88 NO DATA 4.84E-08 2.41E-08 NO DATA NO DATA NO DATA 4.18E-19 W-89 NO DATA. 3.20E-08 2.12E-08 NO DATA NO DATA NO DATA 1.16E-21 5R-89 3.80E-05 NO DATA 1.09E-06 NO DATA NO DATA 1.75E-04 4.37E-05 BR-90 1.24E-02 NO DATA 7.62E-04 NO DATA NO DATA 1.20E-03 9.02E-05
-91 7.74E-09 NO DATA 3.13E-10 NO DATA *NO DATA 4.56E-06 2.39E-05 .-92 8.43E-10 NO DATA 3.64E-11 NO DATA NO DATA 2.06E-06 5.38E-06
(-90 (-91m 2.61E-07 3.26E-11 NO DATA NO DATA 7.01E-09 1.27E-12 NO DATA NO DATA NO DATA NO DATA 2.12E-05 2.40E-07 6.32E-05 1.66E-10 [ (-91 5.78E-05 NO DATA 1.55E-06 NO DATA NO DATA 2.13 E-04 4.81E-05 f-92 1.29E-09 NO DATA 3.77E-11 NO DATA NO DATA 1.96E-06 9.19E-06 f-93 1.18E-08 NO DATA 3.26E-10 NO DATA NO DATA 6.06E-06 5.27E-05 ER-95 1.34E-05 4.30E-06 2.91E-06 NO DATA 6.77E-06 2.21E-04 1.88E-05 ER-97 1.21E-08 2.45E-09 1.13 E'-09 NO DATA 3.71E-09 9.84E-06 6.54E-05 4595 1.76E-06 9.77E-07 5.26E-07 NO DATA 9.67E-07 6.31E-05 1.30E-05 40-99 NO DATA 1.51E-08 2.87E-09 NO DATA 3.64E-08 1.14E-05 3.10E-05 rC-99m 1.29E-13 3.64E-13 4.63E-12 NO DATA 5.52E-12 9.55E-08 5.20E-07 rC-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-_6 0 RU-106 8.64E-06 NO DATA 1.09E-06 NO DATA 1.67E-05 1.17E-03 1.14E-04 NG-110m 1.35E-06 1.25E-06 7.43E-07 NO DATA 2.46E-06 5.79E-04 3.78E-05 PE-125m 4.27E-07 1.98E-07 5.84E-08 1.31E-07 1.55E-06 3.92E-05 8.83E-06
- TE-127m 1.5BE-06 7.21E-07 1.96E-07 4.11E-07 5.72E-06 1.20E-04 1.87E-05 rE-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. 4 5 E-0 4 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
$E-131m 8.74E-09_ 5.45E-09 3.63E-09 6.88E-09 3.86E-08 1.82E'05 6.95E-05 TE-131 1.39E-12 7.44E-13 4.49E-13 1.17E-12 5.46E-12 1.74E-07 2.30E-09 k LINTON-1 3-51 Rev.16-12/97
CPS-ODCM TABLE 3.5-4 (continued) INilALATION DOSE FACTORS FOR ADULT - ( DFA ) , i (mrem per pCi inhaled) NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI TE-132 3.25E-08 2.69E-08 2.02E-08 2.37E-08 1.82E-07 3.60E-05 6.37E-05 I-130 5.72E-07 1.68E-06 6.60E-07 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 .I-132 1.45E-07 4.07E-07 1.45E-07 1.43E-05 6.48E-07 NO DATA 5.08E-08 I-133 1.08E-06 1.85E-06 5.65E-07 2.69E-04 3.23E-06 NO DATA 1.11E-06 I-134 8.05E-08 2.16E-07 7.69E-08 3.73E-06 3.44E-07 NO DATA 1.26E-10 I-135 3.35E-07 8.73E-07 3.21E-07 5.60E-05 1.39E-06 NO DATA 6.56E-07 CS-134 4.66E-05 1.06E-04 9.10E-05 NO DATA 3.59E-05 1.22E-05 1.30E-06 CS-136 4.88E-06 1.83E-05 1.38E-05 NO DATA 1.07E-05 1.50E-06 1.46E-06 CS-137 5.98E-05 7.76E-05 5.35E-05 NO DATA 2.78E-05 9.40E-06 1.05E-06 CS-138 4.14E-08 7.76E-08 4.05E-08 NO DATA 6.00E-08 6.07E*09 2.33E-13 BA-139 1.17E-10 8.32E-14 3.42E-12 No DATA 7.78E-14 4.70E-07 1.12E-07 BA'140 4. 8 8 E-06 6.13 E-09 3.21E-07 NO DATA 2.09E-09 1.59E-04 2.73E-05 BA-141 1.25E*11 9.41E-15 4.20E-13 NO DATA 8.75E-15 2.42E-07 1.45E-17 BA-142 3.29E-12 3.38E-15 2.07E-13 NO DATA 2.86E-15 1.49E-07 1.96E-26 LA-140 4.30E-06 2.17E-08 5.73E-09 NO DATA NO DATA 1.70E-05 5.73E-05 LA-142 8.54E-11 3.88E-11 9.65E-12. NO DATA NO DATA 7.91E-07 2.64E-07 CE-141 2.49E-06 1.69E-06 1.91E-07 NO DATA 7.83E-07 4.52E-05 1.50E-05 CE-143 2.33E-08 1. 72 E-08 1.91E-09 NO DATA 7.60E-09 9.97E-06 2.83E CE-144 4.29E-04 1.79E-04 2.30E-05 NO DATA 1.06E-04 9.72E-04 1.02E-04 PR-143 1.17E-06 4.69E-07 5.80E-08 NO DATA 2.70E-07 3.51E-05 2.50E-05 PR-144 3.76E-12 1.56E-12 1.91E-13 NO DATA 8.81E-13 1.27E-07 2.69E-18 ND-147 6.59E-07 7.62E-07 4.56E-08 NO DATA 4.-07 2.76E-05 2.16E-05 W-187 1.06E-09 8.85E-10 3.10E-10 NO' DATA N U _;1 3 A 3.63E-06 1.94E-05
-239 2.87E-08 2.82E-09 1.55E-09 No DATA 8.U E-09 4.70E-06 1.49E-05 *2.27 x 10" **Less than 10-*'
CLINTON-1 3-52 Rev.16-12/97
CPS-ODCM , TABLE 3.5-5 GROUND PLANE DOSE FACTORS - DFG i (mrem /hr per pCi/m*) SLEMENT TOTAL BODY SKIN !!-3 0.0 0.0 2-14 0.0 0.0 in-24 2.50E-08* 2.90E-08 P-32 0.0 0.0 Cr-51 2.20E-10 2.60E-10 4n-54 5.80E-09 6.80E-09 in-56 1.10E-08 1.30E-08 Pa-55 0.0 0.0 Pc.-59 8.00E-09 9.40E-09 Co-58 - 7.00E-09 8.20E - ho-60 1.70E-08 2.00E-08 Ri-63 - 0.0 0.0 31-65 3.70E-09 4.30E-09
- u-64 1.50E-09 1.70E-09 In-65 4.00E-09 4.60E-09 !
En-69 0.0 0.0 3r-83 6.40E-11 l 9.30E-11 ' %r-84 1.20E-08 1.40E-08 3r-85 0.0 0.0 lb-86 6.30E-10 7.20E-10 ; b-88 3.50E-09 4.00E-09 lb-89 3r-89 1.50E-08 1.80E-08 f ) 5.60E-13 6.50E-13 1 3r-91 7.10E-09 8.30E-09 ) 3r-92 9.00E-09 1.00E-08 l (-90 2.20E-12 2.60E-12 (-91m 3.80E-09 4.40E-09 (-91 2.40E-11 2.70E-11 (-92 1.60E-09 1.90E-09 (-93 5.70E-10 7.80E-10 pr-95 5.00E-09 5.80E-09 Br-97 5.50E-09 6.40E-09 Jb-95 5.10E-09 6.00E-09 po-99 1.90E-09 2.20E-09 [c-99m 9.60E-10 1.10E-09 . pc-101 2.70E-09 3.00E-09 tu-103 3.60E-09 4.20E-09 lu-105 4.50E-09 5.10E-09 lu-106 1.50E-09 1,80E-09 ig-110m 1.80E-00 2.10E-08 1 lLINTON-1 3-53 Rev.16-12/97
CPS-ODCM l j TABLE 3.5-5 (Continued) GROUND PLANE DOSE FACTORS - DFGi (mrem /hr per pCi/m') 1
^
ELEMENT TOTAL. BODY SKIN To-125m 3.50E-11 4.80E-11 'To-127m 1.10E-12 1.30E-12 To-127 1.00E-11 1.10E-11 Te-129m 7.70E-10 9.00E-10 To-129 7.10E-10 8.40E-10 To-131m 8.40E-09 9.90E-09 To-131 2.20E-09 2.60E-06 Te-132 1.70E-09 2.00E-09 I-130 1.40E-08 1. 7 0E - I-131 . 2.80E-09 3.4'0E-09 I-132 - - -1.7DE-08 2.00E-08 I-133 - 3.70E-09 4.50E-09 I-134 1.60E-08 1.90E-08 i I-135 1.20E-08 1.40E-08 Cc-134 1.20E-08 1.40E-08 Co-136 1.50E-08 1.70E-08 Cg-137 4 20E-09 4.90E-09 Cs-138 2.10E-08 2.40E-08 Bn-139 2.40E-09 -
" 2.70E-09 Ba-140 2.10E-09 2.40E-09
')h-141 4.30E-09 4.90E-09 B2-142 7.90E-09 9.00E-09 La-140 1.50E-08 1.70E-08
-L2-142 1.50E-08 1.80E-08 Co-141 5.50E-10 6.20E-10 Co-143 2.20E-09 2.50E-09 Ca-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 W-187 3.10E-09 3.60E-09 Np-239 9.50E-10 1.10E-09
- 2. 50 X 10 " .
J'
)
CLINTON-1 3-54 Rev.16-12/97
1 C PS - ODCM I l TABLE 3.5-6 e INGESTION DOSE FACTORS FOR INFANT - (DFLi ) , (mrem per pCi ingested) HUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI H-3 NO DATA 3.00E-07 3.00E-07 3.00E-07 3.08E-07 3.00E-07 3.08E-07 C-14 2.37E-05* 5.06E-06 5.06E-06 5.06E-06 5.06E-06 5.06E-06 l 5.06E-06 NA-24 1.01E-05 1.01E-05 1.01E-05 1.01E-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-00 9.20E-09 2.01E-09 1.79E-08 4.11E-07 HN-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 7.03-07 NO 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 3.00E-05 5.30E-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 2.57E-05 TI-63 6.34E-04 3.92E-05 2.20E-05 NO DATA NO DATA NO DATA 1.95E-06 1I-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 ZH-65 1.84E-05 6.31E-05 2.91E-05 NO DATA 3.06E-05 NO DATA 5.33E-05 YN-69 9.33E-08 1.68E-07 1.25E-08 NO DATA 6.98E-08 NO DATA 1.37E-05 1R-83 NO DATA NO DATA 3.63E-07 NO DATA NO 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 Bs40E-05 NO DATA NO DATA NO DATA 4.34E-06 RB-88 NO DATA 4.90E-07 2.73E-07 NO DATA NO DATA NO DATA 4.85E-07 RB-89 NO DATA 2.86E-07 1.97E-07 NO DATA NO DATA NO DATA 9.74E-00 OR-89 2.51E-03 NO DATA 7.20E-05 NO DATA NO DATA NO DATA 5.16E-05 ER-90 1.85E-02 NO DATA 4.71E-03 NO DATA NO DATA NO DATA 2.31E-04
'R-91 5.00E-05 NO DATA 1.81E-06 NO DATA NO DATA NO DATA 5.92E-05 A-92 1.92E- U NO DATA 7.13E-07 NO DATA NO DATA NO DATA 2.07E-04
??-90 8.69E-06 NO DATA 2.33E-09 NO DATA NO DATA NO DATA 1.20E-04 .f 8-91m 8.10E-10 NO DATA 2.76E-11 NO DATA NO DATA NO DATA 2.70E-06 if-91 1.13E-06 NO DATA 3.01E-08 NO. DATA NO DATA NO DATA 8.10E-05 R-92 7.65E-Of NO DATA 2.15E-10 NO DATA NO DATA NO DATA 1.46E-04 G-93 2.43E-08 NO DATA 6.62E-10 NO DATA NO DATA NO DATA 1.92E-04 ZR-95 2.06E-07 5.02E-08 3.56E-08 NO DATA 5.41E-08 NO DATA 2.50E-05 j 9R-97 1.48E-00 2.54E-09 1.16E-09 NO DATA 2.56E-09 NO DATA 1.62E-04 NB-95 4.20E-08 1.73E-08 1.00E-08 NO DATA 1.24E-08 NO DATA 1.46E-05 MO-99 NO DATA 3.40E-05 6.63E-06 NO DATA 5.08E-05 NO DATA 1.12E-05 TC-99m 1.92E-09 3.96E-09 5.10E-08 NO DATA 4.26E-08 2.07E-09 1.15E-06 l TC-101 2.27E-09 2.86E-09 2.83E-08 NO DATA 3.40E-08 1.56E-09 4.86E-07 l RU-103 1.48E-06 NO DATA 4.95E-07 NO DATA 3.00E-06 NO DATA 1.80E-05 RU-105 1.36E-07 NO DATA 4.58E-08 NO DATA 1.00E-06 NO DATA 5.41E-05 RU-106 2.41E-05 NOn"A 3.01E-06 NO DATA 2.85E-05 NO DATA 1.83E-04 l AG-110m 9.96E-07 7.'. ' 4.81E-07 NO DATA 1.04E-06 NO DATA 3.77E-05 TE-125m 2.33E-05 7.754 ao 3.15E-06 7.84E-06 NO DATA NO DATA 1.11E-05 . TE-127m 5.85E-05 1.94E-05 7.00E-06 1.69E-05 1.44E-04 NO DATA 2.36E-05 TE-127 1.00E-06 3.35E-07 2.15E-07 8.14E-07 2.44E-06 NO DATA 2.10E-05 TF-129m 1.00E-04 3.43E-05 1.54E-05 3.84E-05 2.50E-04 NO DATA 5.97E-05 TE-129 2.84E-07 9.79E-08 6.63E-08 2.38E-07 7.07E-07 NO DATA 2.27E-05 TE-131m 1.52E-05 6.12E-06 5.05E-06 1.24E-05 4.21E-05 NO DATA 1.03E-04 TE-131 1.76E-07 6.50E-08 4.94E-08 1.57E-07 4.50E-07 NO DATA 7.11E-06 ( - CLINTON-1 3-55 Rev.16-12/97
I l CPS-ODCM TABLE 3.5-6 (continued) INGESTION DOSE FACTORS FOR INFANT - (DFL ) . T (mrem per pCi ingested) NUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI TE-132 2.08E-05 1.03E-05 9.61E-06 1.52E-05 6.44E-05 NO DATA 3.81E-05 I-130 6.00E-06 1.32E-05 5.30E-06 1.48E-03 1.45E-05 NO DATA 2.83E-06 I-131 3.59E-05 4.23E-05 1.86E-05 1.39E-02 4.94E-05 NO DATA 1.51E-06 -
. I-132 1.66E-06 3.37E-06 1.20E-06 1.58E-04 3.76E-06 NO DATA 2.735-06 I-133 1.25E-05 1.82E-05 5.33E-06 3.31E-03 2.14E-05 NO DATA 3.08E-06 I-134 8.69E-07 1.78E-06 6.33E-07 4.15E-05 1.99E-06 NO DATA 1.84E-06 +
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 7.10B-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 2.055-06 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 1.25E-06 BA-139 8.81E-07 5.84E-10 2.55E-08 NO DATA 3.51E-10 3.54E-10 5.58E-05 BA-14C 1.715-04 1.71E-07 8.81E-06 NO DATA 4.06E-08 1.05E-07 4.20E-05 BA-141 4 r25E-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 LA-140 2.11E"-08 8.32E 2.14E-09 NO DATA NO DATA NO DATA 9.77E-05 LA-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 2.48E-05 CE-143 1.48E-08 9.82E-06 1.12E-09 NO DATA 2.86E-09 NO DATA 5. 7 3E-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-10 1.06E-10 1.385-11 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 NO DATA NO DATA NO DATA 3.69E-05
-239 1.11E-08 9.93E-10 5.61E-10 NO DATA 1.98E-09 NO DATA 2.87E-05
*2.37 x 10~
**Less than 10-"
6 I CLINTON 3-56 Rev.16-12/97
PS-ODCM TABLE 3.5-7 INGESTION DOSE FACTORS FOR CilILD - (DFLi ), (mrem per pCi ingested) JCLEDE BONE L1VER T. BODY THYROID KIDNEY LtTNG GI-LL1
-3 NO DATA 2.03E-07 2.03E-07 2.03E-07 2.03E-07 -14 1.21E-05* 2.42E-06 2.03E-07 2.03E-07 2.42E-06 2.42E-06 2.42E-06 2.42E-06 2.42E-06 A-24 5.80E-06 5.80E-06 5.80E-06 5.80E-06 5.80E-06 5.80E-06 -32 8.25E-04 5.80E-06 3.86E-05 3.18E-05 NO DATA NO DATA NO DATA 2. 2 8 E-05 R-51 NO DATA NO DATA 8.90E-09 4.94E-09 1.35E-09 4-54 9.02E-09 4.72E-07 NO DATA 1.07E-05 2.85E-06 NO DATA 3.00E-06 NO DATA 8.90E-06 4-56 NO DATA 3.24E-07 7.54E-08 NO DATA- 4.04E-07 NO DATA 4.84E-05 E-55 1.15E-05 6.10E-06 1.89E-06 NO DATA NO DATA 3.45E-06 E-59 1.65E-05 2. 67 E-05 1.13E-06 1.33E-05 NO DATA NO DATA 7.74E-06 2.78E-05 >-58 NO DATA 1.80E-06 5.51E-06 NO DATA NO DATA 3-60 NO DATA 5.29E-06 NO DATA 1.05E-05 1.56E-05 NO DATA NO DATA NO DATA 2.93E-05 E-63 5.38E-04 2.88E-05 1.83E-05 NO DATA NO DATA 2.22E-06 NO DATA 1.94E-06 I-65 2.09E-07 '1.22E-07 NO DATA NO DATA NO DATA 2.56E-05 J-64 NOL. DATA 2.45E-07 1.48E-07 NO DATA 5.92E-07 NO DATA 1.ISE-05
(-65 1.37Ev05 3.65E-05 2.27E-05 NO DATA 2.30E-05 NO DATA G A1E-06 (-69 4.38E'08 6.33E-08 5.85E-09 NO DATA 3.84E-08 NO DATA 3.99E-06 R-83 NO DATA NO DATA 1.71E-07 NO DATA NO DATA R-8 4 NO DATA LT E-24** NO DATA NO DATA 1.98E-07 NO DATA NO DATA NO DATA LT E-24 It-85 NO DATA,. NO DATA 9.12E-09 NO DATA NO DATA 5-86 NO DATA LT E-24 NO DATA 6.70E-05 4.12E-05 NO DATA NO DATA NO DATA 4.31E-06 5-88 NO DATA 1.90E-07 1.32E-07 NO DATA NO DATA 5-89. NO DATA 9.32E-09 NO DATA 1.17E-07 1.04E-07 NO DATA NO DATA NO DATA 1.02E-09 R-89 1.32E-03 NO DATA 3.77E-05 NO DATA NO DATA R-90 1.70E-02 NO DATA 5.11E-05 NO DATA 4.31E-03 NO DATA NO DATA NO DATA 2.29E-04 i-91 2.40E-05 NO DATA 9.DGE-07 NO DATA NO DATA NO DATA t-92 5.30E-05 9.03E-06 NO DATA 3.62E-07 NO DATA NO DATA NO DATA 1.71E-04
-90 4.11E-08 -91m -91 3.82E-10 NO DATA NO DATA 1.10E-09 1.39E-11 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA 1.17E-04 7.48E-07 f
6.02E-07 NO DATA 1.61E-08 NO DATA NO DATA NO DATA
-92 3.60E-09 8.02E-05 NO DATA 1.03E-10 NO DATA NO DATA NO DATA 1.04E-04 -93 1.14E-08 NO DATA 3.13E-10 NO DATA NO DATA NO DATA 1.70E-04 R-95 1.16E-07 2.55E-08 2.27E-08 NO DATA 3.65E-08 4-97 NO DATA 2.66E-05 6.99E-09 1.01E-09 5.96E-10 NO DATA 1.45E-09 NO DATA 1.53E-04 b-95 2.25E-08 8.76E-09 6.26E-09 NO DATA 8.23E-09 3-99 NO DATA 1.62E-05 NO DATA 1.33E-05 3.29E-06 .NO DATA 2.84E-05 NO DATA 1.10E-05 -99m 9.23E-10 1.81E-09 3.00E-08 NO DATA 2.63E-08 9.19E-10 1.03E-06
- -101 1.07E-09 1.12E-09 1. 42 E-08 NO DATA 1.91E-08 5.92E-10 3.56E-09 J-103 7.31E-07 NO DATA 2.81E-07 HO DATA 1.04E-06 NO DATA J-105 1.89E-05 6.45E-08 NO DATA 2.34E-08 NO DATA 5.67E-07 NO DATA 4.21E-05 J-106 1.17E-05 NO DATA 1.46E-06 NO DATA 1.58E-05 NO DATA 1.82E-04 3-110m 5.39E-07 3.64E-07 2.91E-07 NO DATA 6.78E-07 NO DATA 4.33E-05 E-125m 1.14E-05 3.09E-06 1.52E-06 3. 2 0E- 06 NO DATA NO DATA 1.10E-05 E-127m 2.89E-05 7.78E-06 3.43E-06 6.91E-06 8.24E-05 NO DATA 2.34E-05 -
E-127 4.71E-07 1.27E-07 1.01E-07 3.26E-07 1.34E-06 NO DATA 1.04E-05 E-129m 4.87E-05 1.36E-05 7.56E-06 1.57E-05 1.43E-04 NO DATA 5.94E-05 E-129 1.34E-07 3.74E-08 3.18E-08 9.56E-08 3.92E-07 NO DATA 8.34E-06 $-131m 7.20E-06 2.49E-06 2.65E-06 5.12E-06 2.41E-05 NO DATA 1. 01 E- 0 4 E-131 8.30E-00 2.53E-08 2.47E-08 6.35E-08 2.51E-07 NO DATA 4.36E-07 (- kINTON-1 3-57 1 Rev.16-12/97
I I CPS-ODCM TABLE 3.5-7 (continued) INGESTION DOSE FACTORS FOR CHILD - (DFL ) . f (mrem per pCi ingested) NUCLIDE BONE ' LIVER T. BODY THYROID KIDNEY LUNG GI-LLI TE-132 1.01E-05 4.47E-06 5.40E-06 6.51E-06 4.15E-05 No DATA 4.50E-05 I-130 2. 92 E-06 5.90E-06 3.04E-06 6.50E-04 8. 82E-06 .NO DATA 2.76E-06 I-131 1. 72 E-05 1.73E-05 9.83E-06 5.72E-03 2._84 E-05 NO DATA 1.54E-06 I-132 8.00E-07 1. 47 E-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 1.36E-03 1.22E-05 NO DATA 2.95E-06 I-134 4.19E-07 7.78E-07 3.58E-07 1.79E-05 1.19 E-06 NO DATA 5.16E-07 I-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 3.84:;-04 8.10E-05 NO DATA 1.19E-04 4.27E-05 2.07E-06 CS-136 2.35E-05 6.46E-05 4.18E-05 NO DATA 3.44E-05 5.13E-06 2.27E-06 CS-137 3.27 E-04 3.13E-04 4.62E-05 NO, DATA 1.02E-04 3. 67 E-05 1.96E-06 CS-138 2.28E-07 3.17E-07 2.01E-07 HO 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 BA-140 8.31E-05 7.28E-08 4.85E-06 NO DATA 2.37E-08 4.34E-08 4.21E-05 BA-141 2. DOE-07 1.12E-10 6.51E-09 NO DATA 9.69E-11 6.58E-10 1.14E-07 BA-142 0.74E-08 6. 29 E-11 4.88E-09 NO DATA 5.09E-11 3.70E-11 1.14E-09 LA-140 1.01E-08 3'. 5 3 E-09' 1.10 E NO' DATA NO DATA NO DATA 9.84E-05 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 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 ND-147 2.79E-08 2.26E-08 1.75E-09 NO DATA 1.24E-08 NO DATA 3.58E-05
'W-187 4.29E-07 2.54E-07 1.14E-07 NO DATA NO DATA NO DATA 3.57E-05 ., -239 5.25E-09 3. 77 E-10 2.65E-10 NO DATA 1.09E-09 NO DATA 2.79E-05
- l . 21 x 10*
** Loss than 10-** )'
I l CLINTON-1 3-58 Rev.16-12/97
CPS-ODCM TABLE 3.5-8 INGESTION DOSE FACTORS FOR TEEN - (DFLi ),
) (mrem per pCi ingested) 4UCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI 4-3 NO DATA 1.06E-07 1.06E-07 1.06E-07 1.06E-07 1.06E-07 -14 1.06E-07 4.06E-06* 8.12E-07 8.12E-07 8.12E-07 8.12E-07 0.12E-07 8.12E-07 4A-24 2.30E-06 2.30E-06 2.30E-06 2.30E-06 2.30E-06 2.30E-06 2.30E-06 P-32 2.76E-04 1.71E-05 1.07E-05 NO DATA NO DATA NO DATA 2.32E-05 R-51 NO DATA NO DATA 3.60E-09 2.00E-09 7.89E-10 5.14E-09 6.05E-07 4N-54 NO DATA 5.90E-06 1.17E-06 NO DATA 1.76E-06 NO DATA 1.21E-05 4N-56 NO DATA 1.58E-07 2.81E-08 NO DATA FE-55 2.00E-07 NO DATA 1.04E-05 3.78E-06 2.68E-06 6. 2 5 E-07 NO DATA NO DATA 1.70E-06 1.16E-06 PE-59 5.87E-06 1.37E-05 5.29E-06 NO DATA NO DATA 4.32E-06 3.24E-05 00-58 NO. DATA 9 . 72E-07 2.24E-06 NO DATA NO DATA NO DATA 1.34E-05 20-60 NO DATA 2.81E-06 6.33E-06 NO DATA NO DATA NO DATA 3.66E-05 (I-63 1.77E-04 1.25E-05 6.00E-06 NO DATA NO DATA NO DATA 1.99E-06 41-65 7.49E-07 9.57E-08 4.36E-08 NO DATA NO DATA NO DATA 5.19E-06
- U-64 NO DATA 1.15E-07 5.41E-08 NO DATA 2.91E-07 NO DATA 8.92E-06 EN-65 5.76E,06 2.00E-05 9.33E-06 NO DATA 1.28E-05 NO DATA 8. 4'lE-06 EN-69 1.47E-08 2.80E-08 1.96E-09 NO DATA BR-83 1.83E-08 NO DATA 5.16E-08 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 B.R- 85 NO DATA NO DATA 3.05E-09 NO DATA NO DATA NO DATA LT E-24 RB-8 6 NO DATA 2.98E-05 1.40E-05 NO DATA NO DATA RB-88 NO DATA 4.41E-06 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 BR-89 4.40E-04 NO DATA 1.26E-05 NO DATA NO DATA 5R-90 NO DATA 5.24E-05 8.30E-03 NO DATA 2.05E-03 NO DATA NO DATA NO DATA 2.33E-04 3-91 8.07E-06 NO DATA 3.21E-07 NO DATA NO DATA NO DATA 3.66E-05 A-93 3.05E-06 NO DATA 1.30E-07 NO DATA NO DATA NO DATA 7.77E-05 (-90 (-91m 1.37E-08 1.29E-10 NO DATA NO DATA 3.69E-10 4.93E-12 NO DATA NO DATA NO DATA NO DATA NO DATA 1.13E-04 [ NO DATA 6.09E-09 (-91 2.01E-07 NO DATA 5.39E-09 NO DATA NO DATA NO DATA 8.24E-05 (-92 1.21E-09 NO DATA 3.50E-11 NO DATA NO DATA NO DATA 3.32E-05 (-93 3.83E-09 NO DATA 1.05E-10 NO DATA NO DATA NO DATA 1.17E-04 ER-95 4.12E-08 1.30E-08 -8.94E-09 NO DATA 1.91E-08 NO DATA 3.00E-05 ER-97 2.37E-09 4.69E-10 2.16E-10 NO DATA 7.11E-10 NO DATA 1.27E-04 4B-95 0.22E-09 4.56E-09 2.51E-09 NO DATA 4.42E-09 NO DATA 1.95E-05 40-99 NO DATA 6.03E-06 1.15E-06 NO DATA 1.38E-05 NO DATA 1.08E-05 FC-99m 3.32E-10 9.26E-10 1.20E-08 NO DATA 1.38E-08 5.14E-10 6.00E-07 EC-101 3.60E-10 5.12E-10 5.03E-09 NO DATA 9.26E-09 3.12E-10 8.75E-17 RU-103 2.55E-07 NO DATA 1.09E-07 NO DATA 8.99E-07 NO DATA 2.13E-05 g RU-105 2.18E-08 NO DATA 8.46E-09 HO DATA 2.75E-07 NO DATA 1.76E-05 RU-106 3.92E-06 NO DATA 4.94E-07' NO DATA 7.56E-06 NO DATA 1.88E-04 i AG-110m 2.05E-07 1.94E-07 1.18E-07 HO DATA 3.70E-07 NO DATA 5.45E-05 rE-125m 3.83E-06 1.38E-06 5.12E-07 1.07E-06 NO DATA NO DATA 1.13E-05 PE.127m 9.67E-06 3.43E-06 1.15E-06 2.30E-06 3.92E-05 NO DATA 2.41E-05 rE-127 1.58E-07 5.60E-08 3.40E-08 1.09E-07 6.40E-07 NO DATA 1.22E-05 PE-129m 1.63E-05 6.05E-06 2.58E-06 5.26E-06 6.82E-05 NO DATA 6.12E-05 PE-139 4.48E-08 1.67E-08 1.09E-08 3.20E-08 1.88E-07 NO DATA 2.45E-07 PE-131m 2.44E-06 1.17E-06 9.76E-07 1.76E-0G 1.22E-05 NO DATA 9.39E-05 PE-131 2.79E-08 1.15E-08 8.72E-09 2.15E-08 1.22E-07 NO DATA 2.29E-09
)
l !_ l LINTON-1 3-59 Rev.16-12/97
\
CPS-ODCM TABLE 3.5-8 (continued) INGESTION DOSE FACTORS FOR TEEN - (DFL ) . 3 (mrem per pCi ingested) HUCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI TE-132 3.49E-06 2.21E-06 2.08E-06 2.33E-06 2.12E-05 NO DATA 7.00E-05 I-130 1.03E-06 2.98E-06 1.19E-06 2.43E-04 4.59E-06 NO DATA 2.29E-06 i I-131 5.85E-06 8.19E-06 4.40E-06 2.39E-03 1.41E-05 NO DATA 1.62E-06 1-132 2.79E-07 7.30E-07 2.62E-07 2.46E-05 1.15E-06 NO DATA 3.18E-07 I-133 2.01E-06 3.41E-06 1.04E-06 4.76E-04 5.98E-06 NO DATA 2.58E-06 1-134 1.46E-07 3.87E-07 1.39E-07 6.45E-06 6.10E-07 NO DATA 5.10E-09 I-135 6.10 E-07 1.57E-06 5.82E-07 1.01E-04 2.48E-06 NO DATA 1.74E-06 CS-134 8.37E-05 1. 97 E- 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 C5-137 1.12E-04 1.49E-04 5.19 E-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 4.05E-09 HO DATA 9.22E-11 6.74E-11 1.24E-06 BA-140 2.84E-05 3.4BE 1.83E-06 NO. DATA 1.18E-08 2.34E 4.38E-05 BA-141 6.91E-09 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 DAT? 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 l 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 l 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
.C-187 1.46E-07 1.19E-07 4.17E-08 NO DATA NO DATA NO DATA 3.22E-05 **P-239 1.76E-09 1.66E-10 9.22E-11 NO DATA 5.21E-10 NO DATA 2.67E-05 I .. *4.06 x 10" l **Less than 10~**
l l l l l I n. CLINTON-1 3-60 Rev.16-12/97
PS-ODCM - TABLE 3.5-9 . INGESTION DOSE FACTORS FOR ADULT - (DFL ), j (mrem per pCi ingested) l UCLIDE BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI m3 NO DATA 1.05E-07 1.05E-07 1.05E-07 1.0$E-07 1.0$E-07 1.05E-07 ~ I 014 2.84E-06* 5.68E-07 5.68E-07 5.68E-07 5.68E-07 5.68E-07 5.68E-07 A-24 1.70E-06 1.70E-06 1.70E-06 1.70E-06 1.70E-06 1.70E-06 1.70E-06 i
=32 1.93E-04 1.20E-05 7.46E-06 NO DATA NO DATA NO DATA 2.17E-05 l 3-51 NO DATA NO DATA 2.66E-09 1.59E-09 5.86E-10 3.53E-09 6.69E-07 '
H-54 NO DATA 4.57E-06 8.72E-07 NO DATA 1.36E-06 NO DATA 1.40E-05 H-56 NO DATA 1.15E-07 2.04E-08 NO DATA 1.46E-07 NO DATA 3.67E-06 IE-55 2.75E-06 1.90E-06 4.43E-07 NO DATA NO DATA 1.06E-06 1.09E-06 E-59 4.34E-06 1.02E-05 3.91E-06 NO DATA NO DATA 2.85E-06 3.40E-05 O-58 No DATA 7.45E-07 1.67E-06 NO DATA NO DATA NO DATA 1.51E-05 0-60 NO DATA 2.14E-06 4.72E-06 NO DATA NO DATA NO DATA 4.02E-05 l' 8-63 1.30E-04 9.01E-06 4.36E-06 NO DATA NO DATA NO DATA 1.88E-06 8-65 5.20E-07 6.86E-08 3.13E-08 NO DATA NO DATA NO DATA 1.74E-06 lU-64 NO DATA 8.33E-08 3.91E-08 NO DATA 2.10E-07 NO DATA 7;IOE-06 IN-65 4.84E-06 1.54E-05 6.96E-06 NO DATA 1.03E-05 NO DATA 9670E-06 GD-69 1.03E-08 1.97E-08 1.37E-09 NO DATA 1.20E-08 NO DATA 2.96E-09 3-83 NO DATA NO DATA 4.02E-08 NO DATA NO DATA NO DATA 5.79E-08 3-84 NO DATA NO DATA 5.21E-08 NO DATA NO DATA NO DATA 4.09E-13 @ 85 NO DATA NO DATA 2.14E-09 NO DATA NO DATA NO DATA LT E-24**. 5-86 NO DATA 2.11E-05 9.83E-06 NO DATA NO DATA NO DATA 4.16E-06 h-88 NO DATA 6.05E-08 3.21E-08 NO DATA NO DATA NO DATA 8.36E-19 IB-89 NO DATA 4.01E-08 2.82E-08 NO DATA NO DATA NO DATA 2.33E-21 Q-89 3.08E-04 NO DATA 8.84E-06 NO DATA NO DATA NO DATA 4.94E-05 Q-90 7.58E-03 NO DATA 1.86E-03 NO DATA NO DATA .NO DATA 2.19E-04 W-91 5.67E-06 NO DATA 2.29E-07 NO DATA NO DATA NO DATA 2.70E-05 2-92 2.15E-06 NO DATA 9.30E-08 NO DATA NO DATA NO DATA 4.26E-05 b90 9.62E-09 NO DATA 2.58E-10 NO DATA NO DATA NO DATA 1.02E-04 f P91m 9.09E-11 NO DATA 3.52E-12 NO DATA NO DATA NO DATA 2.67E-10 f=91 1.41E-07 NO DATA 3.77E-09 NO DATA NO DATA NO DATA 7.76E-05 , 'o92 8.45E-10 NO DATA 2.47E-11 NO DATA NO DATA NO DATA 1.40E-05 ) '- 93 2.68E-09 NO DATA 7.40E-11 NO DATA NO DATA NO DATA 8.50E-05 R-95 3.04E-08 9.75E-09 6.60E-09 No DATA 1.53E-08 NO DATA 3.09E-05 R-97 1.68E-09 3.39E-10 1.55E-10 NO DATA 5.12E-10 NO DATA 1.05E-04 L-95 6.22E-09 3.46E-09 1.86E-09 NO DATA 3.42E-09 NO DATA 2.10E-05 b-99 NO DATA 4.31E-06 8.20E-07 NO DATA 9.76E-06 NO DATA 9.99E-06 fC-99m 2.47E-10 6.98E-10 8.89E-09 NO DATA 1.06E-08 3.42E-10 4.13E-07 'C-101 2.54E-10 3.66E-10 3.59E-09 NO DATA 6.59E-09 1.87E-10 1.10E-21 LU-103 1.85E-07 NO DATA 7.97E-08 NO DATA 7.06E-07 NO DATA 2.16E-05 tU-105 1.54E-08 NO DATA 6.00E-09 NO DATA 1.99E-07 NO DATA 9.42E-06 tU-106 2.75E-06 NO DATA 3.48E-07 NO DATA 5.31E-06 NO DATA 1.78E-04 kG-110.n 1.60E-07 1.48E-07 0.79E-08 NO DATA 2.91E-07 NO DATA 6.04E-05 'E-125m 2.68E-06 9.71E-07 3.59E-07 8.06E-07 1.09E-05 NO DATA 1.07E-05 , 'E-127m 6.77E-06 2.42E-06 8.25E-07 1.73E-06 2.75E-05 NO DATA 2. 2 7 E- 0 5 'E-127 1.10E-07 3.95E-00 2.30E-08 8.15E-08 4.48E-07 NO DATA 8.68E-06 E-129m 1.15E-05 4.29E-06 1.82E-06 3.95E-06 4.80E-05 NO DATA 5.79E-05 'E-129 3.14E-08 1.18E-08 7.65E-09 2.41E-08 1.32E-07 NO DATA 2.37E-08 E-131m 1.73E-06 8.46E-07 7. 05 E-07 1.34E-06 0.57E-06 NO DATA 8.40E-05 lE-131 1.97E-08 8.23E-09 6.22E-09 1.62E-08 8.63E-08 NO DATA 2.79E-09
)
LINTON-1 3-61 Rev.16-12/97
CPS-ODCM i TABLE 3.5-9 (continued) I INGESTION DOSE FACTORS FOR ADULT - (DFL ) , 3 (mrem per pCi ingested) NUCLIDE BONE
- LIVER T. BODY- THYROID KIDNEY LUNG GI-LLI 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 I-131 4.16E-06 5.95E-06 3.41E-06 1.95E-03 1.02E-05 NO DATA 1.57E-06 I-132 2.03E-07 5.43E-07 1.90E-07 1.90E-05 8.65E-07 NO DATA 1.02E-07 I-133 1.42E-06 2. 47 E- 06 7.53E-07 3.63E-04 4.31E-06 NO DATA 2.22E-06 I-134 1.06E-07 2.88E-07 1.03E-07 4.99E-06 4.58E-07 NO DATA 2.51E-10 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-08 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 3.56E-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 3.0CE-26 IA-140 2.50E-09 1. 2 6 E 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 HO DATA 2.42E-05 CE-143 1.65E-09 1. 22 E-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 HO DATA 4.03E-05 PR-144 3.01E-11 1. 2 S E-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 . 25 E-0,9 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 6.45E-11 NO DATA 3.65E-10 NO DATA 2.40E-05 i '*2.84 x 10 " -
**Less than 10~2' CLINTON-1 3-62 Rev .16- 12 / 9'l
C PS-ODCM TABLE 3.5-10 , INPUT PARAMETERS FOR CALCULATING R.y Parameter. , Value' Table
- Or(kg/ day) 50 for cow E-3 6 for goat j th,(liters /yr) -
Infant 330 E-5 I
- Child 330 E-5
- Teen 400 E-5 Adult 310 E-5 Yp (kg/m*) 0.7 E-15 Ys (kg/m') 2.0 E-15 j Pa(daya/ liter)' Each stable element for cow E-1 f Each stable element for goat E-2 -
r(dimensioni ss) 1.0 for radioiodine E-15 0.2 for particulates E-15 tr (caconds) 1.73 x 10*(2 days) E-15 ta(caconds) 7.78 x 10'(90 days) E-15
- f. (dim:nsionless) 1.0 for cow NUREG -
1.0 for goat 0133 , Section 5.3.1.3 f p(dimensionless) 1.0 for cow NUREG - 1.0 for goat 0133 -{ Section 5.3.1.3 2of Regulatory Guide 1.109 unless otherwise stated l l l l w CLINTON-1 3-63 Rev.16-12/97
CPS-ODCM TABLE 3.5-11 l INPUT PARAMETERS FOR CALCULATING R",y Parameter , Value Table
- U,p (lite rs/yr) - Infant 0 E-5
- Child 41 E-5
- Teen 65 E-5
- Adult 110 E-5 Fr (days / kg) Each stable element E-1 t.(seconds) 1.73E+06 (20 days) E-15 tn(seconds) 7.78E+06 (90 days) E-15 Yp (kg/m') 0.7 E-15 Y, ( kg/m* ) 2.0 E-15 r(dimensionless) 1.0 for radioiodine E-15 0.2 for particulates E-15 Or(kg/ day) 50 E-3 l
*of Regulatory Guide 1.109
, l
) \
CLINTON-1 3-64 Rev.16-12/97
S-ODCM TABLE 3.5-12 s INPUT PARAMETERS FOR CALCUIATING R* o rameter , Value Table * (
, (kg/yr) -
Infant 0 E-5
- Child 26 E-5
- Teen 42 E-5
- Adult 64 E , (kg/yr) - Infant 0 E-5
- Child 520 E-5
- Teen 630 E-5
- Adult 520 E-5 (dimensionless) 1.0 E-15 (dimensionless) 0.76 E-15 (seconds) -- '
8.6 x 10* (1 day) E-15 (seconds)- 5.18 x 10' (60 days) E-15 (kg/m*) 2.0 E-15 if Regulatory Guide 1.109 ( I b1NTON-1 3-65 Rev.16-12/97
3dS-OO3H i ivnIca C
- s- T E INHVI'V1 ION dVIHMVA 3V31 OHSg - H% )IN3VNI(
( )maam/ AT. da T. itoT/m (
'1HAHOIG XIGN3A IYfND DI-ITI OHDVN8 GON3 I'IA3H 1*GOGA Is01Od3 9'PL3+OZ.
N-E NO GVIV 9*tt3+OZ* 9*tL3+0Z, 9'tL3+0Z. 9*tt3+0Z. 9*tL3+02+ S*CI3+0E S*EZ3+0E S*EI3+0E S*E13+0E S*EI3+0E S*EI3+0E 3-IP Z*9S3+09 I*093+09 MV-ZP I*093+ot I*093+0> I'093+09 I*093+09 I*093+0t I*093+09 Z*0E3+09 I*IZ3+OS L*Lt3+09 NO GM1V NO GM1V NO OVIV I*9I3+09 d-EZ I'Z03+0D C*SL3+02 3H-SI NO GY1V NO GVIV 9*6S3+01 S*LS3+OI I*EZ3+OI Z*SE3+09 t*693+0E NO QVIV t*683+0E I*003+09 L*093+0E HN-SD NO QVIV I*St3+00 Z'ZI3-01 NO QVIV I*T03+00 I'Z93+09 L*IE3+09 HN-99 NO GVIV I*063+0E I*It3+0t E*EE3+0E NO QVIV NO GVIV 9*963+09 J3-SS I*6L3+ot I*023+09 Z*t03+09 J3-96 I*E93+09 Z*ES3+07 6*t93+0E NO QVIV NO QVIV NO GviV I'ZZ3+0E I'9Z3+0E NO UM1V NO GM1V L*Lt3+OS I*It3+09 30-99 E*I63+0> 30-90 NO QVIV 8*OZ3+0E I*193+0t NO GVIV MO GVIV >*SI3+09 Z*0t3+ot I*193+09 NO QVIV NO GM1V Z*063+OS Z*tZ3+OE NI-9E C*E63+OS Z*063+00 E'993-01 I*ZE3-OT NO GW1V NO GVIV 9*IE3+0E S*OI3+0t I NI-9S I*S03+07 NO GV4V I'993+00 L*Lt3-OI NO QVIV E*693+00 6*E03+OE 3n-9F 9*tt3+OS 2N-9S I*6E3+09 9*E93+0t E*II3+09 NO GM1V E'ZS3+09 S*It3409 S*E63-OZ 6*9L3-OZ L*I93-OE NO GVIV t*033-OZ I*tL3+0E I*EZI+09 2N-96 NO GVIV I'II * )1-IS *
- 3H-SE NO QVIV HO GVIV E'913+0E NO GMIV NO QVIV NO QVIV t*003+02 NC QVIV NO GMIV NO QVIV I'II
- P S *IS' 3H-9P NO GVIV NO GM1V NO OVIV Z*093+01 NO GVIV NO QVIV NO GVIV I'II
- t2 *IS MH-SS NO GVIV E*093+OE ME-99 NO QVIV I*603+OS 9*8Z3+09 NO QVIV NO QVIV NO W1V S*SL3+0Z Z*SL3+0Z NO GVIV NO QVIV NO QVIV E*E63+07 HS-SS E'Z13+OZ Z*093+OZ NO GVIV - NO GVIV NO GVIV 9*9Z3+01 UE-96 NO GV4V E*693+OS NO GVIV I*It3+09 NO QVIV NO GVIV Z*0E3+09 9*)03+09 SU-96 I*EI3+OS
.F-60 t*063+OL NO GVIV Z*563+09 NO QVIV NO QVIV I*IZ3+OL 6'993+01 NO QVIV E*993+00 NO GVIV NO QVIV S*Z93+01 L*Et3+09
(' U-61 NO GVIV E*613-01 NO GVIV NO GVIV Z*E93+0t I*t03+OS SU-6Z I*093+OI I*0>3+OS J-60 E*Z63+0E NO QVIY 9*923+01 NO QVIV NO QVIV Z*963+0S NO GVIV I*E63-OZ NO QVIV NO GVIV Z*t63+0E Z*ES3+0E 1-6IW )*OL3-01 S*993+OS NO QVIV I*SL3+0t NO QVIV NO QVIV Z*ts3+09 L*0E3+0t 1 I'ZL3+OS 1-6Z I'993+OI NO GV1Y )*9I3-01 NO QVIV NO GVIV Z*tS3+06 l NO GYIV NO GVIV L*993+0t I*9L3+09 1-6E I*S03+OZ NO GVIV t*OL3+00 Z*0E3+0t NO 3Y1V C*II3+0t I'LS3+09 Z*IL3+OP 2H-6S I*IS3+OS Z*t63+09 2H-6L I*S03+02 E'993+01 I*It3+OI NO GVIV Z*S63+01 I*T03+OS I't03+OS N"-6S I*SL2+ot 9*tE3+0E E*t93+0E NO GVIV )*L33+0C )*L63+0S I*Et3+09 HO-66 NO QVIV I'953+02 E'ZE3+01 NO QVIV Z*9S3+OZ I*ES3+0S )*9L3+09 Z*993-0E C*LZ3-OZ NO QVIV E*II3-OZ 8'II3+02 E'0E3+0E 13-66W I*t03-0E 13-10t 9*S13-OG 8'ZC3-0S 8'IZ3-OD NO GV1V 6*t63-09 S'973+0Z 8*>t3+02 un-10 Z*033+0E NO GVIV 9*L63+OZ NO GVIV t'Z)3+0E S'933+OS I'9I3+09 I'ZZ3+00 NO GVIV t*103-OI NO GVIV 8*663-01 I*St3+09 t'9t3+09 un-IO _* NO GVIV I*0t3+OS I*I93+OL I'9>3+OS gn- M9 8*993+09 NO GVIV I*063+09 YS-IIOW 6*683+0E L*Z23+0E S*003+0E NO QVIV I*063+OP E'9L3+09 E*E03+09 . 13-IZSW >*t93+0E I*663+0E 9*S03+0Z I*923+OE NO QVIV )'tL3+OS I'Z63+OP 12-IZLW I'9L3+09 9*603+0E Z*OL3+0E )*9L3+0E C*LS3+ot I*EI3+09 Z*LE3+09 13-IZL E'ZC3+00 6*SE3-01 )*963-01 I'9S3+00 )*993+00 I*0E3+09 Z*>t3+0t 12-IE6W - I*tI3+09 9*063+0E E'ZE3+OE S*tL3+0E E*I93+0t I'993+09 9*603+07 43-TE6 L*993-OZ C*tL3+OZ I'993-OZ 9*LS3-OZ I'LS3-OT E*003+0E Z*9E3+09 12-IEIW I*0t3+OZ S*S03+OI E'9E3+01 8*6E3+01 Z*9S3+02 I*663+0S I*I63+OS 43-ICI I'Lt3-02 8'Z23-OC S*003-0E I*S03-OZ C*663-OZ Z*093'0E 8*ZZ3+0E l 'l l 3qINION-I E-99 Ua^'I9-IE/6L
l i CPS-ODCM , TABLE 3.5-13 (continued) . INHALATION PATHWAY FACTORS - R*.g (INFANT) (mrem /yr per pCi/m') s )RGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI LSOTOPP PE-1 d 3.72E+02 2.37E+02 1.76E+02 2.79E+02 1.03E+03 3.40E+05 4.41E+04 3-130 6.39E+03 1.39E+04 5.57E+03 1.60E+06 1.53E+04 NO DATA 1.99E+03 [-131 3.79E+04 4.44E+04 1.96E+04 1.48E+07 5.18E+04 NO DATA 1.06E+03 (-132 1.69E+03 3.54E+03 1.26E+03 1.69E+05 3.95E+03 NO DATA 1.90E+03 j-333 1.32E+04 1.92E+04 5.60EF03 3.56E+06 2.24E+04 NO DATA 2.16E+03 1-134 9.21E+02 1.88E+03 6.65E+02 4.45E+04 2.09E+03 NO DATA 1.29E+03 t-135 3.86E+03 7.60E+03 2.77E+03 6.96E+05 8.47E+03 NO DATA 1.83E+03 j0-134 3.96E+05 7.03E+05 7.45E+04 NO DATA 1.90E+05 7.97E+04 1.33E+03
- s-136 4.83E+04 1.35E+05 5.29E+04 NO DATA 5.64E+04 1.18E+04 1.43E+03 pl37 5.49E+05 6.12E+05 '4.55E+04 NO DATA 1.72E+05 7.13E+04 1.33E+03 es-138 5.05E+02 7.81E+02 3.98E+02 NO DATA 4.10E+02 6.54E+01 8.76E+02 h-139 1.48E+00 9.84E-04 4.30E-02 NO DATA 5.92E-04 5.95E+03 5.10E+04 p 140 5.60E+04 5.60E+01 2.90E+03 NO DATA 1.34E+01 1.60E+06 3.84E+04 W-141 1.57E-01 1.08E-04 4.97E-03 NO DATA 6.50E-05 2.97E+03 4.75E+03 YW142 3.9BE-02 3.30E-05 1.96E-03 NO DATA 1.90E-05 1.55E+03 6.9_3E+02 u w140 5.05E+02 2.00E+02 5.15E+01 NO DATA NO DATA 1.68E+05 8.48E+04 142 1.03E+00 3.77E-01 9.04E-02 NO DATA NO DATA 8.22E+03 5.95E+04
.E-141 2.77E+04 1.67E+04 1.99E+03 NO DATA 5.2SE+03 5.17E+05 2.16E+04! ?E-143 2.93E+02 1.93E+02 2.21E+01 NO DATA 5.64E+01 1.16E+05 4.97E+04 SE-144 3.19E+06 1.21E+06 1.76E+05 NO DATA 5.38E+05 9.84E+06 1.48E+05 ?R-143 1.40E+04 5.24E+03 6.99E+02 NO DATA 1.97E+03 4.33E+05 3.72E+04 PR-144 4.79E-02 1.85E-02 2.41E-03 NO DATA 6.72E-03 1.61E+03 4.2BE+03 DD-147 7.94E+03 8.13E+03 5.00E+02 NO DATA 3.15E+03 3.22E+05 3.12E+04 r187 1.30E+01 9.02E+00 3.12E+00 NO DATA NO DATA 3.96E+04 3.56E+04
- P-239 3.71E+02 3.32E+01 1.88E+01 NO DATA 6.62E+01 5.95E+04 2.49E+04 ..
76.47 x 10' ?* Loss than 1.40 x 10-" l l l l $LINTON-1 3-67 Rev.16-12/97
CPS-ODCM TABLE 3.5-14 INilALATION PATilWAY FACTORS - Rh (CllILD)
* (mrem /yr per pCi/m')
T. BODY THYROID KIDNEY LUNG GI-LLI ORGAN: BONE LIVER ISOTOPE 1.12E+03 1.12E+03* 1.12E+03 1.12E+03 1.12E+03 1.12E+03 H-3 NO DATA 6.73E+03 6.73E+03 6.73E+03 6.73E403 6.73E+03 6.73E+03 C-14 3.58E+04 1.61E+04 1.61E+04 1.61E+04 1.61E+04 1.61E+04 1.61E+04 1.61E+04
, NA-24 NO DATA 4.21E+04 2.60E+06 1.14E+05 9.87E+04 NO DATA NO DATA P-32 2.43E+01 1.70E+04 1.08E+03 CR-51 NO DATA NO DATA 1.54E+02 8.54E+01 9.51E+03 NO DATA 1.00E+04 1.58E+06 2.29E+04 MN-54 NO DATA 4.29E+04 1.66E400 3.12E-01 NO DATA 1.67E+00 1.31E+04 1.23E+05 MN-56 NO DATA 2.87E+03 2.52E+04 7.77E+03 NO DATA NO DATA 1.11E+05 FE-55 4.74E+04 1.27E+06 7.07E+04 2.07E+04 3.34E+04 1.67E+04 NO DATA NO DATA FE-59 1.11E+06 3.44E+04 NO DATA 1.77E+03 3.16E+03 NO DATA NO DATA CO-58 7.07E+06 9.62E+04 NO DATA 1.31E+04 2.26E+04 NO DATA NO DATA CO-60 2.73E+05 6.33E+03 8.21E+05 4.63E+04 2.80E+04 NO DATA NO DATA NI-63 8.40E+04 2.96E-01 1.64E-01 NO DATA NO DATA 8.18E+03 NI-65 2.'99E+00 3.67E+04 NO DATA 1.99E+00 1.07E+00 NO DATA . 6.03E+00 9.58E+03 CU-64 9.95E+05 1.63E+04 4.26E+04 1.13E+05 7.03E+04 NO DATA 7.14E+04 EN-65 1.02E+04 6.70E-02 9.66E-02 8.92E-03 NO DATA 5.85E-02 1.42E+03 EM-69 NO DATA LT3. 7 0E-15 *
- NO DATA 4.74E+02 NO DATA NO DATA ER-83 NO DATA LT3.70E-15 NO DATA 5.4BE+02 NO DATA NO DATA NO DATA BR-84 NO DATA NO DATA 2.53E+01 NO DATA NO DATA NO DATA LT3.70E-15 kR-85 NO DATA 7.99E+03 1.98E+05 1.14E+05 NO DATA NO DATA NO DATA RB-86 NO DATA 1.72E+01 5.62E+02 3.66E+02 NO DATA NO DATA NO DATA RB-88 NO "JATA 3.45E+02 2.89E+02 NO DATA NO DATA NO DATA 1.89E+00 RB-89 NO DATA 1.67E+05 NO DATA 1.72E+04 NO DATA NO DATA 2.16E+06 SR-89 5.99E+05 1.48E+07 3.43E+05 1.01E+08 NO DATA 6.44E+06 NO DATA NO DATA ft-90 NO DATA 5.33E+04 1.74E+05
) .41-9 1 1.21E+02 NO DATA 4.59E+00 NO DATA NO DATA 5.25E-01 NO DATA NO DATA 2.40E+04 2.42E+05 "
SR-92 1.31E+01 2.62E+05 2.66E+05 4.11E+03 NO DATA 1.11E402 NO DATA NO DATA Y-90 1.72E+03 1.84E-02 NO DATA NO DATA 2.81E+03 Y-91m 5.01E-01 NO DATA 2.63E+06 1.84E+05 9.14E+05 NO DATA 2.44E+04 NO DATA NO DATA Y-91 NO DATA 2.39E+04 2.39E+05 l Y-92 2.04E+01 NO DATA 5.81E-01 NO DATA 5.11E+00 NO DATA NO DATA 7.44E+04 3.89E+05 Y-93 1.86E+02 NO DATA
- 3. 7 0E+04 NO DATA 5.96E+04 2.23E+06 6.11E+04 ZR ,95 1.90E+05 4.18E+04 3.51E+05 1.13E+05 ER-97 1.88E+02 2.72E+01 1.60E+01 NO DATA 3.89E+01 6.55E+03 NO DATA 8.62E+03 6.14E+05 3.70E+04 NB-95 2.35E+04 9.18E+03 1. 2 7.':+05 1.72E+02 4.26E+01 NO DATA 3.92E+02 1.35E+05 MO-99 NO DATA 9.51E+02 4.81E+03 TC-99m 1.78E-03 3.48E-03 5.77E-02 NO DATA 5.07E-02 1.08E-03 NO DATA 1.45E-03 5.84E+02 1.63E+01 TC-101 8.10E-05 8.51E-05 4.48E+04 NO DATA 1.07E+03 NO DATA 7.03E+03 6.62E+05 RU-103 2.79E+03 1.59E+04 9.95E+04 RU-105 1.53E+00 No DATA 5.55E-01 NO DATA 1.34E+00 1.69E+04 NO DATA 1.84E+05 1.43E+07 4.29E+05 RU-106 1.36E+05 NO DATA 9.14E+03 NO DATA 2.12E404 5.40E+06 1.00E+05 AG-110m 1.69E+04 1.14E+04 3.38E+04 -
2.33E+03 9.14E402 1.92E+03 NO DATA 4.77E+05 TE-125m 6.73E+03 7.14E+04 2.49E+04 8.55E+03 3.02E+03 6. 07 E+ 03 6.36E+04 1.48E+06 TE-127m 1.00E+04 5.62E+04 TE-127 2.77E+00 9.51E-01 6.11E-01 1.96E+00 7.07E+00 6.85E+03 3.04E+03 6.33E403 5.03E+04 1.76E+06 1.82E+05 TE-129m 1.92E+04 2.55E+04 3.50E-02 2.30E-02 7.14E-02 2.57E-01 2.93E403 TE-129 9.77E-02 2.06t+05 3.08E+05 TE-131m 1.34E+02 5.92E+01 5.07E+01 9.77E401 4.00E+02 6.59E-03 1.70E-02 5.88E-02 2.05E+03 1.33E+03 TE-131 2.17E-02 8.44E-03
)
3-68 Re v .16- 12 / 9'? CLINTON-1
PS- ODC11 TABLE 3.5-14 (continued) INilALATION PATIIWAY FACTORS - R* y (CilILD) i (mrem /yr per pCi/m') RGAN: DONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI SOTOPE E-132 '4.81E+02 2.72E+02 2.63E+02 3.17E+02 1.77E+03 3.77E+05 1.38E+05
-130 8.18E+03 1.64E+04 8.44E+03 1.85E+06 2.45E+04 NO DATA 5.11E+03
-131 4.81E+04 4.81E+04 2.73E+04 1.62E+07 7.88E+04 NO DATA 2. 84E+03
-132 2.12E+03 4.07E+03 1.88E+03 1.94E+05 6.25E+03 NO DATA 3.20E+03
-133 1.66E+04 2.03E+04 7.70E4 03 3.85E+06 3.38E+04 NO DATA 5.48E+03
-134 1.17E+03 2.16E+03 9.95E+02 5.07E+04 3.30E+03 NO DATA 9.54E+02
-135 4.92E+0? 8.73E+03 4.14E+03 7.92E+05 1.34E+04 NO DATA 4.44E+03 5-134 6.51E+05 1.01E+06 2.25E+05 NO DATA 3.30E+05 1.21E+05 3.85E+03 S-136 6.51E+04 1.71E+05 1.16E+05 NO DATA 9.55E+04 1.45E+04 4.18E+03 S-137 9.70E+05 8.25E+05 1.28E+05 NO DATA 2.82E+05 1.04E+05 3.62E+03 S-138 6.33E+02 8.40E+02 5.55E+02 NO DATA 6.22E+02 6.81E401 2.70E+02 A-139 1.84E+00 9.84E-04 5.37E-02 NO DATA 8.62E-04 5.77E+03 5.77E+04 A-140 7.40E+04 6.48E+01 4.33E+03 NO DATA 2.11E+01 1.74E+06 1.02E+05 A-141 1.96E-01 1.09E-04 6.36E-03 NO DATA 9.47E-05 2.92E+03 2.75E+02 A-142 5.00E'-02 3.60E-05 2.79E-03 NO DATA 2.91E-05 1.64E+03 2.74E+00 A-140 6.44E+02 2.25E+02 7.55E+01 NO DATA NO DATA 1.83E+05 2.26E+05 A-142 1.30E+00 4.11E-01 1.29E-01 NO DATA NO DATA 8.70E+03 7.59E+04 E-141 3.92E+04 1.95E+05 2.90E+03 NO DATA 8.55E+03 5.44E+05 5.66E+04 E-143 3.66E+02 1.99E+02 2.87E+01 NO DATA 8.36E+01 1.15E+05 1.27E+05 E-144 6.77E+06 2.12E+06 3.61E+05 NO DATA 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+0'4 R-144 5.96E-02 1.85E-02 3.00E-03 NO DATA 9.77E-03 1.57E+03 1.97E+02 D-147 1.08E+04 8.73E+03 6.81E+02 NO DATA 4.81E+03 3.20E+05 0.21E+04 r187 1.63E+01 9.66E+00 4.33E+00 NO DATA NO DATA 4.11E+04 9.10E+04 P-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'
*Less than 3.70 x 10
- 1 (w
- LINTON-1 3-69 Rev.16-12/97 l
C PS -ODCM TABLE 3.b-1S INHALATION PATilWAY FACTORS - Rg (TEEN) 8 (mrem /yr per pCi/m') THYROID KIDNEY LUh'G,, GI-LLI ORGAN: BONE LIVER T. BODY ISOTOPE
- 1. 27 E+ 0 3
- 1.27E+03 1.27E+03 1.27E+03 1.2iE+03 1.27E+03 H-3 NO DATA 4.81E+03 4.87E+03 C-14 2.60E+04 4.87E+03 4.87E+03 4.87E+03 4.87E+03 1.38E+04 1.38E+04 1.38E+04 1.38E+04 1. 3f AE+ 04 1.38E+04 NA-24 1.30E+04 1.10E+05 7.16E4 04 NO DATA NO DATA NO DATA 9.28E+04 P-32 1.89E+06 3.00E+03 NO DATA NO DATA 1.35E+02 7.50E+01 3.07E+01 2.10E+04 CR-51 1.98E+06 6.68E+04 MN-54 NO DATA 5.11E+04 8.40E+03 NO DATA 1.27E+04 1.70E+00 2.52E-01 NO DATA 1.79E+00 1.52E+04 5.74E+04 MN-56 NO DATA 3.34E+04 2.38E+04 5.54E+03 NO DATA NO DATA 1.24E+05 6.39E+03 FE-55 1.53E+06 1.78E+05 FE-59 1.59E+04 3.70E404 1.43E+04 NO DATA NO DATA 2.07E+03 2.784+03 NO DATA NO DATA 1.34E+06 9.52E+04 CO-58 NO DATA CO-60 NO DATA 1.51E+04 1.98E+04 NO DATA NO DATA 8.72E+06 2.59E+05 5.80E+05 4.34E+04 1.98E+04 NO DATA NO DATA 3.07E+05 1.42E+04 NI-63 2.-18 FA00 " 2'.93E-01 1.27E-01 NO DATA NO DATA 9.36E+03 3.67E+04 NI-65 6.14E+04 CU-64 'HO DATA 2.03E+00 8.48E-01 NO DATA 6.41E+00 1.11E+04 3.86L+04 1.34E+05 6.24E+04 NO DATA 8.64E+04 1.24E+06 4.66E+04 ZN-65 4.83E-02 9. 2 0 E-02 6.46E-03 NO DATA 6.02E-02 1.58E+03 2.85E+02 ZN-69 LTBE-15**
NO DATA NO DATA 3.44E+02 NO DATA NO DATA NO DATA ER-83 NO DATA LT8E-15 FR-84 NO DATA NO DATA 4.33E+02 NO DATA NO DATA NO DATA 1.83E+01 No DATA NO DATA NO DATA LTBE-15 LR-85 NO DATA NO DATA 1.77E+04 RB-86 NO DATA 1.90E+05 8.40E+04 NO DATA NO DATA RB-88 NO DATA 5.4GE+02 2.72E+02 NO DATA NO DATA NO DATA 2.92E-05 NO DATA 3.52E+02 2.33E+02 NO DATA NO DATA NO DATA 3.38E-07 RB-89 3.71E+05 SR-89 4.34E+05 NO DATA 1.25E+04 NO DATA NO DATA 2.42E+06 1.08E+08 NO DATA 6.68E+06 NO DATA NO DATA 1.65E+07 7.65E+05 ft-90 6.07E+04 2.59E+05 8.80E+01 NO DATA 3.51E+00 NO DATA NO DATA
).ht-91 NO DATA 4.06E-01 NO DATA NO DATA 2.74E+04 1.19E+05 SR-92 9.52E+00 ,.
Y-90 2.98E+03 NO DATA 8.00E+01 NO DATA NO DATA 2.93E+05 5.59E+05 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 NC 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 ER-97 1.3BE+02 2.72E+01 1.26E+01 NO DATA 4.12E+01 1.30E+05 6.30E+05 N -95 1.86E+04 1.03E+04 5.66E+03 NO DATA 1.00E+04 7.51E+05 9.68E+04 HO-99 HO 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 B.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. ~15 E+ 06 2.73E+05 4.88E+03 2.24E+03 6.67E+02 1.40E+03 NO DATA 5.36E+05 7.50E+04 .
,TE-125m 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 7.28E+00 1.12E+04 8.00E+04 TE-129m 1.39E+04 6.5BE+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 4.02E401 7.25E+01 4.39E+02 2.30E+05 6.21E+05 TE-131 1.5BE-02 8.32E-03 5.04E-03 1.24E-02 6.18E-02 2.34E+03 1.51E+01 i
CLINTON-1 3-70 Rev.16-12/97
- PS-ODCM TABLE 3.5-15 (continued)
INHALATION PATHWAY FACTORS - R*,33 (TEEN) (mrem /yr per pCi/m') ,
\
>RGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI SOTOPE 'E-132 3.60E+02 2.90E+02 2.19E+02 2.46E+02 1.95E+03 4.49E+05
-130 4.63E+05 6.24E+03 1.78E+04 7.17E+03 1.49E+06 2.75E+04 NO DATA 9.12E+03 -131 3.54E+04 4.91E+04 2.64E+04 1.46E+07 8.40E+04 NO DATA 6.49E+03 -132 1.59E+03 4.30E+03 1.58E+03 1.51E+05 6.92E+03 NO DATA 1.27E+03 -133 1.22E+04 2.05E+04 6.22E+03 2.92E+06 3.59E+04 NO DATA 1.03E+04 -134 8.88E+02 2.32E+03 8.40E+02 3.95E*04 3.66E+03 NO DATA 2.04E+01 -135 3.70E+03 9.44E+03 3.49E+03 6.21E+05 1.49E+04 NO DATA 6.95E+03 3-134 5.02E+05 1.12E+06 5.49E+05 NO DATA 3.75E+05 1.46E+05 9.76E+03 3-136 5.15E+04 1.94E+05 1.37E+05 NO DATA 1.10E+05 1.78E+04 1.09E+04 3-137 6. 7 0E+ 05 8.48E+05 3.11E+05 NO DATA 3.04E+05 1.21E+05- 8.48E+03 3-138 4.66E+02 8.56E+02 4.46E+02 NO DATA 6.62E+02 7.87E+01 2.70E-01 A-139 1.34E+00 9.44E-04 3.90E-02 NO DATA 8.88E-04 6.46E+03 6.45E+03 A-140 5.47E404 6.70E+01 3.52E+03 NO DATA 2.20E+01 2.03E+06 2.29E+05 l A-141 1.42E-01 1.06E-04 4.74E-03 NO DATA 9.84E-05 3.29E+03 7.46E-04 A-142 3.70E'-02 3.70E-05 2.27E-03 NO DATA 3.14E-05 1.91E+03 4. 7 9 E-10 A-140 4.79E+02 2.36E+02 6.26E+01 NO DATA NO DATA 2.14E+05- 4.87E+05 A-142 9.60E-01 4.25E-01 1.06E-01 NO DATA NO DATA 1.02E+04 1.20E+04
- E-141 2.84E+04 1.90E+04 2.17E+03 NO DATA 8.88E+03 6.14E+05 1.26E+05
- E-143 2.66E+02 1.94E+02 2.16E+01 NO DATA 8.64E+01 1.30E+05 2.55E+05 lE-14 4 4.89E+06 2.02E+06 2.62E+05 NO DATA 1.21E+06 1.34E+07 8.64E+05 Q-143 1.34E+04 5.31E+03 6.62E+02 NO DATA 3.09E+03 4.83E+05 2.14E+05 R-144 4.30E-02 1.76E-02 2.18E-03 NO DATA 1.01E-02 1.75E+03 2.35E-04 D-147 7.86E+03 8.56E+03 5.13E+02 NO DATA 5.02E+03 3.72E+05 1.82E+05 9187 1.20E+01 9.76E+00 3.43E+00 NO DATA NO DATA 4.74E+04 1.77E+05 P-239 3.30E+02 3.19E+01 1.77E+01 NO DATA 1.00E+02 6.49E+04 1.32E+05 ,
1,27 x 10'
*L3ss than 8.00 x 10-"
i l 1 LINTON-1 3-71 Rev.16-12/97
4 I CPS-CDCM I TABLE 3.5-16 i INilALATION PATilWAY FACTORS - RQ ( ADULT)
~i (mrem /yr per pCi/m')
THYROID KI DN EY_ LUNG GI-LLI ORGAN: DONE ~ LIVER T . BODY _ ISOTOPE 1.26E+03 1.26E+03 1 1.26E+03* 1.26E+03 1.26E+03 1.26E+03 H-3 NO DATA 3.41E+03 3.41E403 3.41E+03 C-14 1.82E+04 3.41E+03 3.41E+03 3.41E403 1.02E+04 1.02E+04 1.02E+04 1.02E+04 1.02E+04 ! HA-24 1.02E+04 1.02E+04 8.64E+04 5.01E+04 NO DATA NO DATA NO DATA P-32 1.32E+06 7.71E+04 3.32E+03 1.00E+02 5.95E+01 2. 2 0 E+ 01 1.44E+04 CR-51 NO DATA NO DATA 7.74E+04 6.30E+03 NO DATA 9.04E+03 1.40E+06 MN-54 NO DATA 3.96E+04 1.83E-01 NO DATA 1.30E+00 9.44E+03 2.02E+04 l MN-56 NO DATA 1.24E+00 7.21E+04 6.03E+03 l
- 1. '7 0 E+04 3.94E+03 NO DATA NO DATA l FE-55 2.46E+04 NO DATA 1.02E+06 1.88E+05 1.18E+04 2.78E+04 1.06E+04 NO DATA l
FE-59 NO DATA 9.28E+05 1.06E+05 CO-58 No DATA 1.58E+03 2.07E+03 No DATA 1.15E+04 1.48E+04 NO DATA NO DATA 5.97E+06 2.0$E+05 f l CO-60 NO DATA 1.78E+05 1.34E+04 l 3.14E+04 1.45E+04 NO DATA NO DATA NI-63 4.32E+05 5.60E+03 1.23E+04 2.10E-01 9.12E-02 NO DATA NO DATA NI-65 1 54E+00 4.62E+00 6.78E+03 4.90E+04 l CU-64 NO DATA 1.46E+00 6.15E-01 No DATA j 4.66E404 NO DATA 6.90E+04 8.64E+05 5.34E+04 ZN-65 3.24E+04 1.03E+05 l 4.52E-03 NO DATA 4.22E-02 9.20E+02 1.63E+01 I ZN-69 3.30E-02 6.51E-02 NO DATA 2.32E+02 I NO DATA 2.41E+02 No DATA NO DATA CR-83 No DATA NO DATA 1.64E-03 NO DATA NO DATA 3.13E+02 NO DATA NO DATA l ( BR-84 NO DATA LT8E-15** I NO DATA 1,20E+01 NO DATA NO DATA L R-85 NO DATA NO DATA 1.66E+04 1.35E+05 5.90E+04 NO DATA NO DATA RB-86 NO DATA NO DATA 3.34E-09 3.87E402 1.93E+02 NO DATA NO DATA RB-88 NO DATA 9.28E-12 1.70E+02 NO DATA NO DATA NO DATA RB-89 NO DATA 2.56E+02 3.50E+05 NO DATA 0.72E+03 NO DATA No DATA 1.40E+06 SR-89 3.04E+05 9.60E+06 *l.22E+05 NO DATA 6.10E+06 NO DATA NO DATA SR-90 9.92E407 3.65E+04 1.91E+05 6.19E+01 NO DATA 2.50E+00 NO DATA NO DATA I SR-91 NO DATA 1.65E+04 4.30E+04 SR-92 6.74E+00 NO DATA 2.91E-01 NO DATA , , 5.61E+01 NO DATA NO DATA 1.70E+05 5.06E+05 Y-90 2.09E+03 NO DATA 1.02E-02 NO DATA NO DATA 1.92E+03 1.33E+00 Y-91m 2.61E-01 NO DATA 3.85E+05 NO DATA 1.24E+04 NO DATA NO DATA 1.70E+06 Y-91 4.62E+05 1.57E+04 "J.35E+04 1.03E+01 NO DATA 3.02E-01 NO DATA NO DATA Y-92 4.85E+04 4.22Evo5 9.44E401 NO DATA 2.61E+00 NO DATA NO DATA Y-93 1.77E+06 1.50E+05 ZR-95 1.07E+05 3.44E+04 2.33E+04 NO DATA 5.42E+04 9.04E+00 NO DATA 2.97E401 7.07E+04 5.23E+05 l ZR-97 9.68E+01 1.96E+01 4.21E+03 NO DATA 7.74E+03 fr . 05E+05 1.04E+05 l NB-95 1.41E404 7.82E+03 2.40E+05 1.21E+02 2.30E+01 NO DATA 2.91E+02 9.12E+04 MO-99 NO DATA 7.64E+02 4.16E+03 t TC-99m 1.03E-03 2.91E-03 3.70E-02 NO DATA 4.42E-02 6.02E-05 5.90E-04 NO DATA 1.08E-03 3.99E+02 1.09E-11 TC-101 4.18E-05 5.05E+05 1.10E+05 RU-103 1.53E+03 NO DATA 6.58E+02 NO DATA 5.83E+03 3.11E-01 NO DATA 1.02E+00 1.10E+04 4.02E+04 RU-105 7.90E-01 NO DATA 9.12E+05 NO DATA 8.72E+03 NO DATA 1.34E+05 9.36E+06 RU-106 6.91E+04 4.63E+06 3.02E405 AG-110m 1.00E+04 1.00E404 5.94E403 NO DATA 1.97E404 l 1.58E+03 4 . 67 E+ 02 1.05E403 1.24E+04 3.14E+05 7.06E404 l TE-125m 3.42E+03 1.50E+05 1.57E+03 3.29E+03 4.5DE+04 9.60E+05 _ TE-127m 1.26Et04 5. 7 7 E+ 03 6.51E+03 5.74E+04 TE-127 1.40E400 6.42L-01 3.10E-01 1.06E+00 5.10E+00 4.67E403 1.5BE+03 3.44E403 3.66E404 1.16E+06 3.03E+05 TE-129m 9.76E403 2.39E-02 1.24E-02 3.90E-02 1.07E-01 1.94E403 1. 57 E+ 0? TE-129 4.98E-02 1. 46E4 05 5. 56E4 05 TE-131m 6.39E401 4.36E+01 2.90E+01 5.50E401 3.09E402 3.59E-03 9.36E-03 4.37E-02 1.39E+03 1.04E+01 TE-131 1.11E-02 5.95E-03 4 I i CLINTON-1 3-72 Rev.16-12/9~7
f
\
CPS-ODCM TABLE 3.5-16 (continued)
- INHALATION PATHWAY FACTORS - R*m (ADULT)
(mrem /yr per pCi/m') ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE TE-132 2.60E+02 2.15E+02 1.62E+02 1.90E+02 1.46E+03 I-130 4.58E+03 2.8BE+05 5.10E+05 1.34E+04 5.28E+03 1.14E+06 2.09E+04 NO DATA I-131 2.52E+04 3.58E+04 2.05E+04 7.69E+03 1.19E+07 6.13E+04 NO DATA 6.28E+03 I-132 1.16E403 3.26E+03 1.16E+03 1.14E+05 5.18E+03 1-133 8.64E+03 NO DATA 4.06E+02 1.48E+04 4.52E+03 2.15E+06 2.58E+04 NO DATA 1-134 6.44Z+02 1.73E+03 6.15E+02 8.88E+03 2.98E+04 2.75E+03 NO DATA 1.01E+00 I-135 2.6BE+03 6.98E+03 2.57E+03 4.48E+05 1.11E+04 CS-134 NO DATA 5.25E+03 3.73E+05 8. 4 8E+05 7.28E+05 NO DATA 2.87E+05 CS-136 3.90E+04 9.76E+04 1.04E+04 1.46E+05 1.10E+05 NO DATA 8.56E+04 1.20E+04 CS-137 4.78E+05 6.21E+05 1.1*lE+ 04 4.2BE+05 NO DATA 2.22E+05 7.52E+04 CS-138 3.31E+02 6.21E+02 3.24E+02 8.40E+03 BA-139 NO DATA 4.80E+02 4.86E+01 1.86E-03 9.36E 6.66E-04 2.74E-02 NO DATA 6.22E-04 3.76E+03 BA-140 3.90E+04 4.90E+01 8.96E+02 2.57E+03 NO DATA 1. 67 E+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. 7 4 E+02 4.58E+01 NO DATA NO DATA 1.36E+05 IA-142 6.83E-01 3.10E-01 4.58E+05 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 CE-143 3.62E+05 1.20E+05 1.86E+02 1.38E+02 1.53E+C NO DATA 6.03E+01
@E-144 3.43E+06 7.98E+04 2.26E+05 1.43E+06 1.84E+J5 NO DATA 8.48E+05 7.78E+06 PR-143 9.36E+03 3.75E+03 8.16E+05 4.64E+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 7.05E-03 1.02E+03 OD-147 5.27E+03 6.10E+03 2.15E-08 3.65E+02 NO DATA 3.56E+03 2.21E+05 1.73E+05 *r-187 8.48E+00 7.08E+00 2.48E+00 NO DATA NO DATA 2.90E+04 1.55E+05 .#-239 2.30E+02 2.26E+01 1.24E+01 NO DATA 7.00E+01 3.76E+04 1.19E+05 .
01.26 x 10' o*Less than 8.00 x 10'25 I l ( ~
- LINTON-1 3-73 Rev.16-12/97
j CPS-ODCM TABLE 3.5-17 I COW MILK PATHWAY FACTORS - R*.n (INFANT)
># (m* rem /yr per pCi/sec)
LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ORGAN: BONE ISOTOPE 2.38E+03* 2.38E+03* 2.38E+03* 2.38E+03* 2.388+03* 2.38E+03* , H-3 No DATA 6.89E+05* ! C-14 3.23E+06* 6.89E+05* 6.89E+05* 6.89E+05* 6.89E+05* 6.89E+05* 1.55E+07 1.55E+07 1.55E+07 1.55E+07 1.55E+07 1.55E+07 . MA-24 1.55E+07** 2.16E+09 1.60E+11 9.41E+09 6.20E+09 NO DATA NO DATA No DATA P-32 2.04E+05 4.69E+06 CR-51 NO DATA NO DATA 1.61E+05 1.05E+05 2.29E+04 3.90E+07 8.84E+06 NO DATA 8.64E+06 NO DATA 1.43E+07 NN-54 NO DATA 3.12E-02 5.39E-03 NO DATA 2.69E-02 NO DATA 2.84E+00 NN-56 NO DATA 1.11E+07 1.35E+08 8.72E+07 2.33E+07 WO DATA NO DATA 4.265+07 FE-55 1.16E+08 1.87E+08 ( FE-59 2.25E408 3.92E+08 1.55E+08 NO DATA NO DATA 2.43E+07 6.06E+07 NO DATA NO DATA NO DATA 6.05E+07 CO-58 NO DATA 8.82E+07 2.00E+08 NO DATA NO DATA NO DATA 2.10E+08 CO-60 NO DATA 1.08E+08 2.16E+09 1.21E+09 NO DATA NO DATA NO DATA NI-63 3.50E+10 3,52E+00 3.98E-01 1.81E-01 NO DATA NO DATA NO DATA 3.03E+01 NI-65 3.11E+05 NO DATA 3.78E+06 CU-64 NO DATA 1.84E+05 8.52E+04 NO DATA 1.91E+10 8. *18 E+09 NO DATA 9.23E+09 NO DATA 1.61E+10 EN-65 5.552+09 1.94E-11 3.49E-11 2.60E-12 NO DATA 1.45E-11 NO DATA 2.85E-09 EN-69 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA CR-83 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA ER-84 NO DATA NO DATA NO DATA NO DATA, NO DATA NO DATA NO DATA BR-85 NO DATA 5.70E+08 2.23E+10 1.10E+10 NO DATA NO DATA NO DATA RB-86 NO DATA 1.83E-44 1.88E-44 1.03E-44 NO DATA NO DATA NO DATA R8-88 NO DATA NO DATA 3.43E-52 2.36E-52 NO DATA NO DATA NO DATA 1.17E-52 RB-89 NO DATA 2.59E+08
-SR-89 1.26E+10 No DATA 3.61E+08 NO DATA NO DATA 3.10E+10 NO DATA NO DATA NO DATA 1.52E+09
$R-90 1.22E+11 NO DATA No DATA 9.76E+03 NO DATA NO DATA NO DATA 3.20E+05
')BR-91 2.71E+05 5.05E+01-NO DATA 1.74E-01 NO DATA NO DATA NO DATA SR-92 4.6BE+00 9.43E+05 - 1.83E+01 NO DATA NO DATA NO DATA Y-90 6.83E+02 NO DATA 6.09E-19 NO DATA 2.08E-20 NO DATA NO DATA NO DATA 2.03E-15 Y-91m NO DATA 5.26E+06 7.33E+04 NO DATA 1.95E+03 NO DATA NO DATA Y-91 NO DATA 1.02E+01 Y-92 5.35E-04 No DATA 1.50E-05 NO DATA NO DATA NO DATA , 5.83E-02 NO DATA NO DATA NO DATA 1.69E+04 Y-93 2.14E+00 8.28E+05 ER-95 6.82E+03 1.66E+03 1.18E+03 NO DATA 1.79E+03 NO DATA 6.96E-01 3.16E-01 NO DATA 7.01E-01 NO DATA 4.41E+04 ER-97 4.03E+00 2.06E+08. Ne-95 5.93E+05 2.44E+05 1.41E+05 NO DATA 1.75E+05 NO DATA 2.01E+08 4.04E+07 NO DATA 3.10E+08 NO DATA 6.83E+07 MO-99 NO DATA 1.64E+04 2.75E+01 5.66E+01 7.29E+02 NO DATA 6.09E+02 2.96E+01 TC-99m 5.81E-57 2.72E-59 3.42E-59 3.39E-58 NO DATA 4.07E-58 1.87E-59 TC-101 1.06E+05 RU-103 8.67E+03 NO DATA 2.92E+03 NO DATA 1.81E+04 NO DATA 2.70E-03 NO DATA 5.88E-02 NO DATA 3.18E+00
'RU-105 8.00E-03 NO DATA 1.45E+06 RU-106 1.91E+05 NO DATA 2.38E+04 NO DATA 2.26E+05 NO DATA 2.81E+08 1.86E+08 NO DATA 4.02E+08 NO DATA 1.46E+10 AG-110m 3.85E+08 NO DATA 7.19E+07
- TE-125m 1.51E+08 5.05E+07 2.04E+07 5.08E+07 NO DATA 1.40E+08 5.10E+07 1.22E+08 1.04E+09 NO DATA 1.70E+08 TE-127m 4.22E+08 NO DATA 1.36E+05 TE-127 6.31E+03 2.11E+03 1.39E+03 5.13E+03 1.58E+04 TE-129m 5.56E+08 1.91E+08 8.56E+07 2.14E+08 1.39E+09 NO DATA 3 . 's 2 E+ 00 9.34E-10 6.33E-10 2.27E-09 6.75E-09 NO' DATA 2.17E-07 i TE-129 2.71E-09 2.29E+07 TE-131m 3.37E+06 1.36E+06 1.12E+06 2.75E+06 9.35E+06 NO DATA 1.29E-32 9.78E-33 3.11E-32 8.91E-32 NO DATA 1.41E-30 TE-131 3.48E-32 1
I CLINTON-1 3-74 Rev.16-12/97
JPS-ODCM e TABLE 3.5-17 (continued) . COW MILK PATHWAY FACTORS - R.g (INFANT) 5 2 (m mrem /yr per pCi/sec) )RGAN: { BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI
- sOTOPE TE-132 2.12E+07 1.05E+07 9.80E+06 1.55E+07 6.57E+07 l
NO DATA 3.89E+07
- -130 3.53E+06 7.76E+06 3.12E+06 8.70E+08 8.53E+06 l
- -131 2.71E+09 NO DATA 1.66E+06 '
3.19E+09 1.40E+09 1.05E+12 3.73E+09 NO DATA 1.14E+08
- -132 1.43E+00 2.90E+00 1.03E+00 1.36E+02 3.24E+00 NO DATA
- -133 3.63E+07 2.35E+00 5.28E+07 1.55E+07 9.60E+09 6.21E+07 NO DATA 8.93E+06 l
- -134 1.64E-11 3.36E-11 1.20E-11 7.86E-10 3.76E-11 1.13E+05 NO DATA 3.48E-11
- -135 2.24E+05 8.18E+04 2.01E+07 2.50E+05 NO DATA 8.12E+04 S-134 3.65E+10 6.81E+10 6.88E+05 NO DATA 1.75E+10 7.19E+09 LS-136 1.97E+09 1.85E+08 5.81E+09 2.17E+09 NO DATA 2.31E+09 4.73E+08 8.82E+07
[S-137 5.15E+10 6.03E+10 4.27E+09 NO DATA 1.62E+10 6. 4 4 E+09 1.89E+08 FS-138 8.06E-23 1.31E-22 6.35E-23 NO DATA 6.53E-23 1.02E-22 2.09E-22 M-139 4.29E-07 2.84E-10 1.24E-08 NO DATA 1.71E-10 1.72E-10_ A-140 2.72E-05 2.~4 5G08 2.45E+05 1.26E+07 NO DATA 5.72E+04 1.50E+05 5.92E+07 %-141 4.16:t;-45 2.85E-48 1.31E-46 NO' DATA 1.71E-48 1.73E-48 5.08E-44 a-142 2.32n-79 1.93E-82 1.14E-80 NO DATA 1.11E-82 1.17E-82 9.56E-79 i A-140 4.050+01 1.60E+01 4.11E+00 NO DATA NO DATA NO DATA 1.88E+05 A-142 1.73E-10 6.34E-11 1.52E-11 NO DATA NO DATA NO DATA 1.08E-05 .E-141 4.34E+04 2.65E+04 3.12E+03 NO DATA 8.17E+03 NO DATA 1.37E+07 l
- E-14 3 3.98E+02 2.64E+05 3.01E+01 NO DATA 7.69E+01 NO DATA 1.54E+06
- E-14 4 2.34E+06 9.56E+05 1.31E+05 NO DATA 3.87E+05 NO DATA, 1.34E+06 9 143 1.49E+03 5.56E+02 7.37E+01 NO DATA 2.07E+02 NO DATA 7.85E+05 '
l 9-144 6.27E-53 2.43E-53 3.16E-54 NO DATA 8.79E-54 NO CATA 1.13E-48 D-147 8.79E+02 9.03S+02 5.53E+01 NO DATA 3.48E+02 NO DATA 5.72E+05 r187 .6.10E+04 4.24E+04 1.46E+04 NO DATA NO DATA NO DATA 2.49E+06 t-239 3.64E+01 3.26E+00 1.84E+00 NO DATA 6.49E+00 NO DATA 9.41E+04 . mrem /yr per pCi/m
*1.55 x 10' l
i i l LINTON-1 3-75 Fev.16-12/97 L
'l
' CPS-ODCM-TABLE 3.5-18 COW MILK PATHWAY FACTORS - R".g (CillLD)
) (m# mrem /yr per pCi/sec)
BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ORGAN I ISOTOPE ~ H-3 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+05* 3.29E+05* 3.29E+05* 3.29E+05* 3.29E+05* 3.29E+05*
.NA-24 8.93E+06** 8.93E+06 8.93E+06 8.93E+06 8.93E+06 8.93E+06 8.93E+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 NN-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 00-58 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 MTA NO DATA NO DATA 2.39E+08 i NI-63 2.97E+10 1.59E+09 1.01E+09 NO DATA NO DATA NO DATA 1.07E+08 l
NI-65 1.65Ef00 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+C5 NO DATA 3.47E+06
- EM-65 4.13Ef09 1.10E+1_0 6.83E+09 NO DATA- 6.92E+09 NO DATA 1.93E+09 EM-69 9.11E-12 1.32E-11 1.22E-12 NO DATA 7.99E-12 NO DATA 8.30E-10 ER-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
-kR-85 NO DATA MO DATA O DATA NO DATE NO DATA NO DATA NC D'EA RB-86 NO DATA 8. 7 8 E+09 5.40E+09 NG DATA NO DATA NO DATA 5.65E+0B 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 1.2SE-57 NO DATA NO DATA NO DATA 1.22E-54 ER-89 6.63E+09 NO DATA 1.89E+08 NO DATA NO DATA NO DATA 2.57E+08 1.12E+11 No DATA 2.84E+10 NO DATA NO DATA NO DATA 1.51E+09 .YLA-91 r90 1.30E+05 No DATA 4.89E+03 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.
T-90 3.23E+02- ND 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 1.04E+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 -
ER-95 3.84E+03 8.44E+02 7.51E+02 NO DATA 1.21E+03 NO DATA 8.80E+05 ER-97' 1.92E+00 2.78E-01 1.64E-01 NO DATA 3.99E-01 NO DATA 4.21E+04 N4-95 3.18E+05 1.24E+05 8.84E+04 NO DATA 1.16E+05 NO DATA 2.29E+08 HD-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 l TC-101 1.28E-59 1.34E-59 1. 7 0 E.-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 l 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 1.13E408 NO DATA 2.63E+08 NO DATA 1.6BE+10 TE-125m 7.39E+07 2.00E+07 9.85E+07 2.07E+07 NO DATA NO DATA 7.13E+07 - TE-127m 2.08E+08 5.61E+07 2.47E+07 1.98E+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 2.71E+0B 7.58E+07 4.21E+07 8.74E407 7.97E+08 NO DATA 3.31E+0B l _TE-129m i TE-129 1.28E-09 3.57E-10 3.04E-10 9.12E-10 3.74E'09 NO DATA 7.96E-08 l TE-131m 1.60E+06 5.53E+05 5.88E+05 1.14E+06 5.35E+06 NO DATA 2.24E+07 TE-131 1.64E-32 5.01E-33 4.89E-33 1.26E-32 4.97E-32 NO DATA 8.63E-32 l-l . CLINTON-l' 3-76 Rev.16-12/97
C PS - ODCM TABLE 3.5-18 (continued) .
- COW MILK PATIIWAY FACTORS - R h (CllILD)
(m* mrem /yr per pCi/sec) 2 ORGAN: BONE LIVER T. BODY Tl!YROID KIDNEY LUNG GI-LLI IISOTOPE
~
TE-132 1.03E+07 4.56E+06 5.51E+06 6.64E+06 4.23E+07 NO DATA 1-130 1.72E+06 3.47E+06 4.59E+07 1.79E+06 3.82E+08 5.19E+06 NO DATA 1.62E+06 1-131 1.30E+09 1.31E+09 7. 4 4 E+ 08 4.33E+11 2.15E+09 NO DATA 1.17 E+ 08 I-132 6.91E-01 1.27E+00 5.84E-01 5.89E+01 1.94E+00 NO DATA I-133 1.72E+07 2.12E+07 1.49E+00 8.03E+06 3.94E+09 3.54E+07 NO DATA 8.56E+06 I-134 7.92E-12 1.47E-11 6.77E-12 3.38E-10 2.25E-11 NO DATA 5.43E+04 9.75E-12 I-135 9.77E+04 4.62E+04 8.56E+06 1.50Et05 NO DATA CS-134 2.27E+10 3.72E+10 7.44E+04 7.85E+09 NO DATA 1.15E+10 4.14E+09 2.01E+08 C7-136 1.01E+09 2.78E+09 1.00E+09 NO DATA 1.48E+09 2.21E+08 C;-137 3.23E+10 9.76E+07 3.09E+10 4.56E+09 HD 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 BA-139 4.02E-24 2.45E-23 2.01E-07 1.08E-10 5.04E-09 NO DATA 9.39E-11 6.33E-11 BA-140 1718&O8 1.16E-05 .
- 1. 03F.+ 05 6.84E+06 NO DATA 3.37E+04 6.12E+04 5. 94 E+0*J BA-141 1.96E-45 1.10P.-48 6.30E-47 NO DATA 9.50E-49 6.45E-48 BA-142 1.10 E'-79 7.93'4-83 1.12E-45 6.15E-81 NO DATA 6.41E-83 4.66E-03 1.AA E- 81 '
IA-140 1.94E+01 6.78E+00 2.11E+00 NO DATA NO DATA NO DATA 1.89E+05 LA-142 8.23E-11 2.62E-11 8.21E-12 NO DATA NO DATA CE-141 2.19E+04 NO DATA 5.20E-06 i.09E+04 1.62E+03 NO DATA 4.78E+03 NO DATA 1.36E+07. CE-143 1.87E+02 1.02E4lJS 1.47E+01 NO DATA 4.26E+01 NO DATA C.E-14 4 1.49E+06-
- 1. 63 E+ 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 t'O DATA 1.17E+02 NO DATA 7.76E+05 PR-144 2.94E-53 9.10E-54 1.48E-54 NO DATA 4.61E-54 NO DATA 1.968-50 ND-147 4.44E+02 3.59E+02 2.78E+01 NO DATA 1.97E+02 NO DATA 5.69E+05
(-187 2.88E+04 1.71E+04 7.66E+03 No DATA NO DATA NO DATA 2.40E+06 stP-23 9 1.72E+01 1.24E+00 0.69E-01 NO DATA 3.58E+00 NO DATA 9.15E+04 , c mrem /yr per pCi/m 3
**8.93 x 10'
( .- CLINTON-1 3-77 Rev.16-12/97
CPS-ODCM I TABLE 3.5-19 COW MILK PATHWAY FACTORS - Rh (TEEN) (m# mrem /yr per pCi) THYROID KIDNEY LUNG GI-LLI ORGAN: BONE LIVER T_. DODY ISOTOPE ~ NO DATA 9.92E+02* 9.92E+02* 9.92E+02* 9.92E+02 A 9.92E+02* 9.92E+02* N-3 1.34E+05* 1.34E+05* C-14 6.70E+05* 1.34E+05* 1.34E+05* 1.34E+05* 1.34E+05* 4.29E+06 4.29E+06 4.29E+06 4.29E+06 4.29E+06 4.29E+06 NA-24 4.29E+06* 1.95E+09 1.22E+09 NO DATA NO DATA NO DATA 2.64E+09 P-32 3.15E+10 8.41E+06 NO DATA NO DATA 5.00E+04 2.78E+04 1.10E+04 7.14E+04 CR-51 NO DATA 2.00E+07 HN-54 NO DATA 1.40E+07 2.78E+06 NO DATA 4.19E+06 HN-56 NO DATA 7.32E-03 1.30E-03 NO DATA 9.26E-03 NO DATA 4.82E-01 4.46E+07 3.16E+07 7.38E+06 NO DATA NO DATA 2.01E+07 1.37E+07 FE-55 3.81E+07 2.68E+08 FE-59 5.18E+07 1.21E+08 4.67E+07 NO DATA NO DATA NO DATA 7.98E+06 1.84E+07 NO DATA No DATA NO DATA- 1".10 E+ 0 8 CO-58 2.78E+07 6.26E+07 NO DATA NO DATA NO DATA 3.62E+0B Co-60 NO DATA 1.33E+08 NI-63 1.18E+10 8.34E+08 4.00E+08 NO DATA NO DATA NO DATA
- 6. '19 E-@l -8;67E-02* 3.95E NO DATA NO DATA NO DATA 4MOE+00 NI-65 3.26E+06 CU-64 NO DATA 4.20E+04 1.97E+04 NO DATA 1.06E+05 NO DATA 7.32E+09 3.41E+09 HO DATA 4.6BE+09 NO DATA 3.10E+09 l IN-65 2.11E+09
! ZN-69 3.70E-12 7.06E-12 4.94E-13 NO DATA 4.61E-12 NO DATA 1.30E-11 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA CR-83 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA CR-84 NO DATA NO DATA NO DATA No DATA NO DATA NO DATA NO DATA ) LR-85 NO DATA RB-86 NO DATA 4.74E+09 2.23E+09 HO DATA NO DATA NO DATA 7.01E+08 l 3.34E-52 NO DATA 3.90E-45 2.08E-45 NO DATA NO DATA NO DATA RB-86 7.90E-53 5.64E-53 NO DATA NO DATA NO DATA 1.22E-61 RB-89 NO DATA 3.19E+08 SR-89 2.68E+09 NO DATA 7.67E+07 NO DATA NO DATA NO DATA 6.62E+10 NO DATA 1.64E+10 NO DATA NO DATA NO DATA 1.86E+09 r-90 2.39E+05 d-91 5.27E+04 NO DATA 2.10E+03 NO DATA NO DATA NO DATA
)SR-92 9.03E-01 NO DATA 3.85E-02 NO DATA NO DATA NO DATA 2.30E+01 ' -
1.31E+02 3.53E+00 NO DATA NO DATA NO DATA 1.08E+06 Y-90 NO DATA Y-91m 1.18E-19 NO 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 2.82E+00 4.10E-01 NO DATA 1.12E-02 NO DATA NO DATA NO DATA 1.25E+04 Y-93 IKt95 1.65E+03 5.20E+02 3.58E+02 NO DATA 7.65E+02 NO DATA 1.20E+06 ER-97 7.87E-01 1.56E-01 7.17E-02 NO DATA 2.36E-01 NO DATA 4.22E+04 NB-95 1.41E+05 7.81E+04 4.30E+04 NO DATA 7.57E+04 NO DATA 3.34E+08 HO-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 2.00E+02 KO DATA 2.39E+02 8.89E+00 1.05E+04
*C-101 5.22E-60 7.42E-60 7.29E-59 NO DATA 1.34E-50 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 . 7 3 E+ 03 NO DATA 7.23E+04 NO DATA 1.80E+06 AG-110m 9.64E+07 9.12F+07 5.$5E+07 NO DATA 1.74E+08 NO DATA 2.56E+10 TE-125m 3.01E+07 1.00E+07 4.02E+06 8.41E+06 NO DATA NO DATA 8.88E+07 -
TE-127m 8.43E+07 2.99E+07 1.00E+07 2.01E+07 3.42E+08 NO DATA 2.10E+08 TE-127 1.21E+03 4.28E+02 2.60E+02 8.33E+02 4.89E+03 NO DATA 9.33E+04 TE-129m 1.10E+08 4.09E+07 1.74E+07 3.56E+07 4.61E+0B 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 2.92E-32 NO DATA 5.50E-34 i t4 J l CLINTON-1 3-78 Rev.16-12/97 l j
PS-ODCM - TABLE 3.5-19 (continued) , COW HILK PATHWAY FACTORS - #R.g (TEEN) (m* mrem /yr per pCi/sec) RGAN: BONE LIVER { T. BODY THYROI D KIDNEY LONG GI-LLI 50 TOPE _ B-132 4.29E+06 2.72E+06 2.56E+06 2.87E+06 2.61E+07 NO DATA 8.61E+07
-130 7.33E+05 2.12E+06 8.47E+05 1.73E+08 3.27E+06 NO DATA -131 5.36E+08 7.50E+08 1.63E+06 4.03E+08 2.19E+11 1.29E+09 NO DATA 1.48E+08 -132 2.90E-01 7.59E-01 2.72E-01 2.56E+01 1.20E+00 NO DATA -133 7.06E+06 1.20E+07 3.31E-01 3.65E+06 1.67E+09 2.10E+07 NO DATA 9.06E+06
-134 3.34E-12 8.86E-12 3.18E-12 1.48E-10 1.40E-11 NO DATA -135 2.29E+04 1.17E-13 5.90E+04 2.19E+04 3.80E+06 9.32E+04 NO DATA 6.54E+04 S-134 5.79E+09 2.30E+10 1.07E+10 NO DATA 7.32E+09 2.80E+09 5-136 4.48E+08 2.87E+08 1.76E+09 1.18E+09 NO DATA 9.59E+08 1.51E+08 1.42E+08 B-137 1.33E+10 1.77E+10 6.18E+09 NO DATA 6.03E+09 2.34E+09 B-138 1.58E-23 2.52E+08 3.03E-23 1.51E-23 NO DATA 2.23E-23 2.60E-24 1.37E-26 A-139 8.20E-08 5.77E-11 2.39E-09 NO DATA 5.44E-11 A-140 4.85E+07
- 3. 9 8 E 7 31E-07 5.95E+04 3.13E+06 NO DATA 2.02E+04 4.00E+04 7.49E+07 A-141 7.98E'-46 5.96E-49 2.67E-47 NO DATA 5.53E-49 4.08E-49 A-142 4.'54E-80 1.70E-51 4.54E-83 2.80E-81 NO DATA 3.85E-83 3.02E-83 1.40E-91 A-140 8.11E+00 3.98E+00 1.06E+00 NO DATA NO DATA NO DATA A-142 3.42E-11 2.29E+05 1.52E-11 3.78E-12 NO DATA NO DATA NO DATA 4.62E E-141 8.88E+03 5.93E+03 6.81E+02 NO DATA 2.79E+03 E-143 7,64E+01 NO. DATA 1.70E+07' 5.55E+04 6.21E+00 NO DATA 2.49E+01 NO DATA 1.67E+06 E-144 6.61E+05 2.73E+05 3.55E+04 NO DATA 1.63E+05 NO DATA R-143 2.91E+02 1.66E+08 1.16E+02 1.45E+01 NO DATA 6.75E+01 NO DATA 9.57E+05 R-144 1.19E-53 4.88E-54 6.04E-55 No DATA. 2.80E-54 NO DATA 1.31E-56 D-147 1.81E+02 1.97E+D2 1.18E+01 NO DATA 1.16E+02
-187 1.19E+04 NO DATA 7.10E+05 9.72E+03 3.41E+03 NO DATA NO DATA NO DATA 2.63E+06 ?-239 6.99E+00 6.59E-01 3.66E-01 NO DATA 2.07E+00 NO DATA 1.06E+05 %
mrem /yr per pCi/m'
- 4.29 x 10' w
LINTON-1 3-79 Rev.16-12/97
3dS-OG3H 1VTH'3 E
- S-Z O 3OM HIIW dVIHMVA 3V31 OHS - E% )V0nI'l(
i{
)m,maam/ Ar. daJ li3T / sad (
1HAUOIG MIGN3A I'DND DI-ITI GON3 I'I A3B 1 900A OMDVN: _IS01Od3 L*9Z3+0Z, L*9Z3+0Z. L*923+OZ, L*9Z3+OZ. NO QVIV L*9Z3+OZ. L*923+OZ. H-E L*E93+09, L*393+0t. L*393+09, t'Z93+0t* E'9E3+OS. L*393+OP, L*393+0>. Z*t93+09 3-It Z*t93+09 Z*t93+09 3*t93+09 Z*t93+09 HV-Zt Z*t93+09,, E*P93+09 NO QVIV I*6Z3+06 I*093+06 9*913+00 NO QVIV NO QVIV d-EZ I*LI3+IO I*L03+09 9'ZL3+0E E*L83+09 L*193+09 NO QVIV NO GVIV Z*0S3+ot 3U-SI I"903+09 NO GVIV Z*S03+09 NO QVIV Z*S03+OL HN-SP NO QVIV 0*tI3+09 I*EE3-OI L*Et3-09 NO GVAV S*E93-OE NO OVIV MN-99 NO GVIV t*It3-OC 6*903+09 6*6S3+09 I*LE3+OL t*093+09 NO QV,TV NO QVIV J3-SS Z*SI3+OL NO QVIV NO UVIV I*693+04 Z*EE3+00 J3-S6 Z*6L3+OL 9*663+0L 3*903+0L NO GVIV NO QVIV NO GVIV 6*St3+OL 30-90 NO GVIV t*LZ3+09 I*0934OL C*003+00 E'923+OL NO QVIV NO QVIV NO QVIV 30-90 HO QVIV I'973+OL HO UVIV 6
- L t 3+OL t ' 9L 3+08 - E ' Z 93+09- NO UVIV NO QVIV NI-9E 9*LE3+06 NO QVIV NO GVIV I'ZZ3+00 E'L03-01 t*OI3-02 Z*I63-OZ NO QVIV NI-99 NO QVIV S*6D3+0P NO GY1V Z*013+09 Z*E93+OP I*II3+0t 3n-9t NO GVlY NO UVIV Z*6E3+06 NO QVIV Z*LS3+06 2N-9S I*EL3+06 P*EL3+06 I*603+06 G*LL3-IC Z*9L3-IC NO UVIV Z*903-IZ NO QVIV 2N-96 Z*013-IZ E*0P3-IZ NO QVIV NO QVIV NO GVIV NO GY1V NO UVIV NO QVIV 2H-GE NO QVIV NO QVIV NO OVIV NO QVIV NO QVIV NO QVIV HO QVIV NO GY1V JH-09 NO UVIV NO GVIV NO OVIV NO QV1V NO QVIV NO QVIV NO GVIV S*I33+00 1H-09 I*ZI3+06 NO W1V NO QVIV NO QVIV MC-09 NO QVIV Z*903+06 HO QVIV Z*6L3-S9 Z'IS3-PS I*It3-PS NO QVIV NO QVIV HH-09 NO QVIV NO QVIV NO QVIV Z*9I3-99 NO QVIV )'t63-GE E*I93-GE NO QVIV M +- 0 6 NO QVIV NO GVIV NO GVIV Z*EE3+00 SU-06 I*t93+06 NO QVIV >'I93+OL I*ES3+06 I*IS3+IO NO QVIV NO QVIV NO GVIV 3-60 t'903+IO NO QVIV I*EL3+09 I*193+0E NO QVIV NO GY1V NO QVIV 7-6I Z*OL3+09 NO QVIV NO QVIV 6*t93+00 -
NO QVIV Z'IE3-OZ NO GY1V NO GVIV SU-6Z t*633-01 NO QVIV NO GY1V NO QVIV L*SE3+OS A-60 L*I03+OI NO QVIV I*603+00 I*063-I6 Z*)63-ZI NO GVIV NO GV1V NO QVIV X-6Im 9*tZ3-ZO MO QVIV NO QVIV )*LE3+09 NO GY1V Z*E03+02 NO QVIV NO GVIV A-61 8*903+0E NO GVIV NO QVIV 6*LS3-OI G*SL3-0S NO QVIV I ' 9C 3-09 NO GVIV A-6E NO OVIV NO QVIV L*0E3+0E A-6E E'ZZ3-OI NO GVIV 9'I23-OE NO GVIV 6*9I3+OS Z*053+02 NO GVIV >*t93+OZ NO QVIV 2u46S 6*tS3+OZ E*0E3+OZ NO QVIV Z*L03+0# 0*LI3-OZ E*S03-OZ NO GVIV I*E33-OI 2U-6L >*EZ3-OI t*993+09 NO GVIV Z*L63+00 8'ZS3+09 )*963+ot Z*tL3+ot NO GVIV NG-69 NO UVIV S'913+OL NO QVIV StLP3+OL NO GVIV Z'P03+OL >*L33+09 S*SE3+0E HO-66 I*I63+02 NO aviV I*PE3+0Z t'S03+00 13-66W E*EI3+00 6*ES3+00 Z*T03-90 I'Zt3-LI
)*II3-90 t*0E3-96 NO GVIV L*tI3-96 13-101 Z*0S3-90 NO QVIV E*063+0C NO GY1V I*163+09 un-IOC I*OZ3+0E NO QVIV P*E63+02 S ZI3-OI E*E93-06 NO QVIV I*I03-OZ NO GVIV un-IOS 0*SZ3-09 NO QVIV NO GV1V I*EZ3+09 Z*093+09 NO QVIV E*G03+0C NO OVIV E'693+0t un-I09 NO GY1V I*093+00 NO GV1Y 2*203+IO S*E63+OL E*203+0L Vs-IIom S*8Z3+OL G*6I3+09 Z*163+09 >*6I3+09 9*9P3+OL NO GVIV 9*SE3+OL _-
13-IZSW I'9E3+OL I*093+00 NO QVIV I'9E3+00 I'993t0L S*S03+09 I*IL3+OL _ 13-IZLm t*S03+OL Z*9S3+0E NO QVIV S*I)3+09 13-IZL 9'SE3+OZ Z*E)3&02 I*tI3+0E P*0E3+0E NO QVIV E*0E3+00 Z*393*OL 6*SZ3+09 Z*OL3+OL Z*S13+00 13-IZ6m 9*013+OL I*I03-06 NO QVIV Z*IZ3-IO I*093-IO 9*093-II Z'I93-IO 13-I26 Z*0Z3-IO Z*L63+OS I*L03+09 NO QVIV I'LS3+OL 13-IEIW E'903+OS I*t93+0S I*PL3+OS S*ZZ3-ED C*0E3-CC I'913-EZ NO GVIV 13-IEI E'903-EE I*St3-CE I*I93-CE k. c-80 ua^'I9-IZ/6L OI" INION-I
PS -ODCM TABLE 3.5-20 (continued) COW MILK PATHWAY FACTORS - RSg (ADULT) (m* mrem /yr per pCi/sec) / LGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI LOTOPE
;-132 2.41E+06 1.56E+06 1.46E+06 1.72E+06 1.50E+07 NO DATA 7.36E+07 130 4.16E+05 1.23E+06 4.84E+05 1.04E+08 131 1.91E+06 NO DATA 1.06E+06 2.9*JE+08 4.24E+08 2.43E408 1.39E+11 7.27E+08 NO DATA 132 1.12E+08 1.65E-01 4.40E-01 1.54E-01 1.54E+01 7.02E-01 NO DATA 8.27E-02
~
133 3.86E+06 6.72E+06 2.05E+06 9.87E+08 1.17E+07 NO DATA 6.04E+06 134 1.89E-12 5.13E-12 1.83E-12 8.88E-11 8.15E-12 NO DATA 135 1.29E+04 4.47E-15 3.39E+04 1.25E+04 2.23E+06 5.43E+04 NO DATA 3.83E+04 l-134 5.67E+09 1.35E+10 1.10E+10 NO DATA 2.64E+08 4.37E+09 1.45E+09 2.36E+08 l-136 1.04E+09 7.49E+08 NO DATA 5.79E+08 7.94E+07 1.18E+08 l-137 7.39E+09 1.01E+10 6.62E+09 NO DATA 3.43E+09 1.14E+09 1.96E+08 l-138 8.69E-24 '1.72E-23 8.50E-24 NO DATA 1.26E-23 1.24E-24 L-139 4.43E-08 3.16E-11 7.32E-29 1.30E-09 NO DATA 2.95E-11 1.79E-11 E 86E-08 . L-140 2;722+07 3.42E+04 1.78E-06 NO DATA 1.16E+04 1.96E+04 5.60E+07 L-141 4. 33E-4 6 3.27E-49 1.46E-47 NO DATA t-142 3.04E-49 1.86E-49 2.04E-55 2.51E-80 2.58E-83 1.58E-81 NO DATA 2.18E-83 1.46E-83 3.54E-98 - L-140 4.53E+00 2.28E+00 6.03E-01 NO DATA NO DATA NO DATA 1.67E+05 t-142 1.09E-11 8.61E-12 2.15E-12 NO DATA NO DATA l-141 4.84E+03 NO DATA 6.29E-08 3.27E+03 3.71E+02 No DATA 1.52E+03 NO DATA 1.25E+07
- -143 4.16E+01 3.07E+04 3.40E+00 NO DATA 1.35E+01 NO DATA 1.15E+06 l-144 3.58E+05 1.50E+05 1.92E+04 NO DATA L-143 8.87E+04 NO DATA 1.21E+08 1.58E+02 6.35E+01 7.84E+00 NO DATA 3.66E+01 NO DATA 6.93E+05 L-144 6.47E-54 2.69E-54 3.29E-55 NO DATA 1.52E-54 NO DATA
>-14 7 9.44E+01 .9.31E-61 1.09E+02 6.53E+00 NO DATA 6.38E+01 NO DATA 5.24E+05 -187 6.50E+03 5.43E+03 1.90E+03 NO DATA NO DATA NO DATA 1.78E+06 6-239 3.67E+00 3.60E-01 1.99E-01 NO DATA ' 1.1.2 E+ 00 NO DATA 7.39E+04 rtrem/yr per pCi/m'
- 2. 4 6 x 10'
( .- bINTON-1 3-81 Rev.16-12/97
i b<S-OI(3H 1VHI"3 C*G-ZI DOVL. HIIW dVIHMVA 3V31OUS - U% )IN3VNI(
)w,aam/ AJ daa ir3T/ sac (
(( 1'IA3H LHAUOIG XIGN3A I'nND DI-ITI OHDVN: GOHW 1 900A IS01Od3 H-E NO GV1Y t*993+0E, >*893+0E. t*993+0E. >*893+0E. t*993+0E. t*993+0E. 3-IP C*EC3+09, 9*863+0S, 9*863+05 9*963+09, 9*863+09, 9*863+09, 9*963+05 MV-ZD I*SL3+09,, I'8L3+09 I'8L3+09 I
- 9L 3+09 I*8L2+09 I*eL3+09 I 963+09 I*IE3+IO L*t93+06 NO GM1V NO GM1V NO GVIV Z*993+06 d-EZ I*603+II Z*t93+09 S*9E3+OS 3U-SI NO UY1V NO QVIV I*6E3+09 I*393+09 Z*LS3+0E NN-SD NO GVIV - t'993+09 I*093+09 NO GVIV I*073+09 NO GY1V I'LZ3+09 HN-99 NO GVIV E'LS3-0E 9*t93-09 NO GVIV E*ZZ3-OE NO GVIV E*t03-01 I*LS3+09 I
- IE3409 C*0Z3+OS NO OVIV NO uviV S*SE2+OS I'tt3+OS J3-SS J3-96 Z*613+09 S*093+09 Z*003+09 'NO GW1V NO UV1V I*S03+09 Z*PE3+09 00-59 NO GVIV Z*603+09 L*Zt3+09 NO GNIV NO GviV NO GVIV L*ZC3+09 30-90 NO GVIV I*093+OL' Z*t63+OL NO GVIV MO GM1V NO UVIV Z*913+OL NI-9E )*163+06 Z*963+09 I*t53+09 NO GM1V MO UVLY- NO GVIV I*363+OL NI-95 )*Z03-OI-- t
- t 93-02-- Z'I93-OZ-
- NO GNIV .NO GM1V -NO M Y C*9Z3+00 3n-99 MO QVIV Z*093+09 6*t93+0E NO GW1V E'* t S3+OP NO GVIV >*163+09 3N-95 9*999+08 Z*Z93+06 I*053+06 NO QVIV I*103+06 MO QVIV I*633+06 3N-96 Z*EZ3-IZ )*193-IZ C*T13-IE NO GVIV I'Lt3-IZ NO GNIV E*tI3-10 3H-8E NO GVIV NO MV NO GVIV NO GNIV NO GNIV NO QVIV NO GVIV l 9H-89 NO GW1V MO QVIV NO QVIV NO GNIV NO GMIV NO UVIV NO GVIV f t*H-8S NO GNIV NO GMIV NO GVIV NO GNIV NO GM1V NO QVIV NO GN1V ME-99 NO QVIV Z*9S3+06 I*EI3+06 NO GM1V NO GVIV MO GVIV 9*t63+OL HS-99 NO MY E'Z53-ts I*ZE3-PS NO QVIV NO GVIV NO QVIV Z*163-PS ME-96 NO MV )*063-SE Z*8Z3-SE NO GNIV NO GNIV NO UVIV I*E63-SE 3H-86 Z*9t3+IO .MO M V L*993+09 NO GV1V NO MV NO QVIV S*tE3+08 Z*SS3+II NO QVIV 9*S03+IO NO OVIV NO MV NO GY1V E*I63+06
.dH-60 (REM-61 9*953+0S NO GV1V Z*053+0t NO GVIV NO GNIV NO GVIV 9'963+05 f EM-6E 6*9E3+00 NO QVIV E'9S3-01 NO GMIV NO GMIV NO MV I*093+0Z~
A-60 8*163+01 NO GVIV Z*163+00 NO UY1V NO UVIV NO GNIV I*IE3+OS ' 1-6IW L*363-ZO NO GY1V Z*t83-ZI NO OVIV NO GMIV NO UVIV Z*tE3-19 A-6I 8*t83+0E NO GVIV Z*Et3+OZ NO UVIV NO GM1V NO GNIV 9*Z63+09 A-63 9't03-OS NO QVIV I*903-09 NO QVIV NO GVIV NO QVIV I*Z33+00 A-6E Z*SS3-OI NO GW1V 9*693-0E NO GNIV NO GM1V NO GVIV Z*0E3+0E 3H-6S 8*193+OZ I*663+0Z I*tI3+0Z NO GVIV Z*It3+0E NO GVIV 6*603+ot 3H-6L t*8S3-01 8*EE3-OZ E*903-OZ NO QVIV 8*t03-OZ NO GNIV S*EI3+OE N"-6S L*IE3+09 Z*6E3+0D I'963+09 NO GM1V Z*T03+0t NO GviV Z*tL3+OL HO-66 NO QVIV Z
- t 9 3+OL )*893+09 NO GM1V E'L13+OL NO QVIV 8*183+09 13-66M E*E93+00 9*LE3+00 8*9L3+OI NO GM1V L*Et3+01 E*SE3+00 I*693+OE 13-I01 C*E93-90 t*II3-90 t*093-96 NO GVIV t'983-56 Z*393-90 9*G83-58 Hn-10E I*093+0E NO GVIV E*tt3+0E NO GVIV Z*193+0E NO GY1V I*393+09 un-IOS 6*903-09 NO QVIV E'ZE3-09 NO QVIV L*093-OE NO QVIV E*833-OI un-109 Z*393+09 NO GVIV Z*993+0E NO GVIV Z*963+09 NO GVIV I*LE3+OS VD-IIOW )*9Z3+OL C*Et3+OL Z*ZE3+OL NO GVIV t*8E3+OL NO QVIV I'LS3+06 12-IESW I*803+OL 9*033+09 Z*tC3+09 9'093+09 NO QVIV NO GVIV 8*S93+09
- 13-TELW 9*093+OL I'9L3+OL 9*T03+09 I'993+OL I*Et3+09 NO GNIV Z*0E3+OL
{ I'9E3+OZ 9*193+0Z I*8S3+OE NO GVIV I'963+09 i 13-IZL L*SL3+0E Z*St3+0E 13-136W 9'983+OL Z*Z63+OL I*0E3+OL Z*SL3+OL I*9L3+09 NO GV1V E*663+00 ,__ 13-136 E*Z53-IO I*I23-IO l'S63-II Z*LE3-IO 8*T03-IO NO*GVIV Z*903-09 13-IEIW >*093+OS I*9E3+OS I*E93+OS E*E03+OS I*IE3+09 HO GV1V Z*L)3+09 13-IEI t*163-EE I*SS3-EE I*193-EE E*tt3-EE I*OC3-EZ NO QVIV I'963-EI
- 1 C
3qINION-I C-8Z ua^*I9-TZ/6L
CPS-ODCM
- TABLE 3.5-21 (continued) ,
GOAT MILK PATHWAY FACTORS - R*g3 (INFANT) (m* mrem /yr per pCi/sec) ORGAN: BONE LIVER T. BODY THYROID , KIDNEY LUNG GI-LLI ISOTOPE TE-132 2.54E+06 1.26E+06 1.17E+06 1.85E+06 7.86E+06 NO DATA 4.65E+06 T-130 4.22E+06 9.28E+06 3.73E+06 1.04E+09 1.02E+07 NO DATA 1.99E+06
- I-131 3.25E+09 3.83E+09 1.69E+09 1.26E+12 4.48E+09 NO DATA 1 37E+08 I-132 1.73E+00 3.50E+00 1.25E+00- 1.64E+02 3.91E+00 NO DATA 2.84E+00 I-133 4.34E+07 6.32E+07 1.85E+07 1.15E+10 7.43E+07 NO DATA 1.07E+07 I-134 1.97E-11 4.04E-11 1.44E-11 9.42E-10 4.52E-11 NO DATA 4.18E-11 I-135 1.36E+05 2.70E+05 9.85C+04 2.42E+07 3.01E+05 NO DATA 9.77E+04 c5-134 1.09E+11 2.04E+11 2.06E+10 NO DATA 5.25E+10 2.15E+10 5.54E+08 CS-136 5.92E+09 1.74E+10 6.50E+09 NO DATA 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 i BA-139 5.14E-08 3.41E-11 1.49E-09 NO DATA 2.05E-11 .2.07E-11 3.,26E-06
~
BA-140 2.17E+07 -2.87E+04 1.48E+06 NO DATA 6.82E+03 1.76E+04 7 06E+06 BA-141 4.97Ef46 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 T4E-73 ~ LA-140 4.83E+00 1.91E+00 4.90E-01 NO DATA NO DATA NO DATA 2.24E+04 IA-142 2.07E-11 7.60E-12 1.82E NO DATA NO DATA NO DATA 1.29E-06 { CE-141 5.20E+03 3.17E+03 3.73E+02 NO DATA 9.78E+02 NO DATA 1.64E+06. 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+G5 1.14E+05 1.56E+04 NO DATA 4.61E+04 NO DATA 1.60E+07 l PR-143 1.78E+02 6.66E+01 8.83E+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 r187 7.27E+03 5.06E+03 1.75E+03 NO DATA NO DATA NO DATA 2.97E+05 P-239 4.37E+00 3.91E-01 2.21E-01 NO DATA 7.80E-01 NO DATA 1.13E+04 {g '
- mrem /yr per pCi/m3
**1.87 x 10' l
- j i
CLINTON-1 3-83 Rev.16-12/97
C PS-ODCM TABLE 3.5-22 GOAT MILK PATHWAY FACTORS - Rh (CHILD)
<) (m* mrem /yr per pCi/sec)
THYROID KIDNEY . LUNG GI-LLI ORGAN: BONE LIVER T. BODY ISOTOPE 3.20E+03* 3.20E+03* 3.20E+03* NO DATA 3.20E+03* 3.20E+03* 3.20E+03* H-3 3.29E+05* 3.29E+05* 3.29E+05* 3.29E+05* C-14 1.65E+06* 3.29E+05* 3.29E+05* 1.07E+06 1.07E+06 1 07E+06 1.07E+06 1 07E+06
-NA-24 1.07E+06** 1.07E+06 2.58E+09 3.59E+09 NO DATA NO DATA NO DATA P-32 9.32E+10 4.36E+09 6.47E+05 NO DATA 1.22E+04 6.77E+03 1.85E+03 1.' 24 E+ 04 CR-51 NO DATA 7.05E+05 NO DATA 2.11E+06 NO DATA 2.51E+06 6.7 0E+05 NO DATA HN-54 1.85E-03 NO DATA 1.21E-01 HN-56 NO DATA 1.53E-03 3.45E-04 NO DATA 1.42E+05 7.65E+05 2.38E+05 NO DATA NO DATA 4.35E+05 FE 1.45E+06 NO DATA 7.29E+05 2.62E+06 -FE-59 1.55E+06 2.52E+06 1.25E+06 NO DATA 4.46E+06 NO DATA NO DATA NO DATA 8.49E+06 CO-58 NO DATA 1.46E+06 2.86E+07 1.52E+07 NO DATA NO DATA NO DATA CO-60 NO DATA 5.16E+06 NO DATA 1.28E+07 1.90E+08 .1.21E+0B . NO DATA -NO DATA NI-63 _3.55E+09 NO DATA NO DATA 2.29E+00 N1-65 1.99E'01 1.87E-02 1.095-02 NO DATA 3.86E+05 4.97E+03 NO DATA 1.99E+04 NO DATA CU-64 NO DATA 8.23E+03 2.32E+08 8.22E+08 NO DATA 8.33E+08 NO DATA EN-65 4.96E408 1.32E+09 9.94E-11 1.465-13 NO DATA '9.56E-13 NO DATA EM-69 1.09E-12 1.58E-12 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 MO DATA NO DATA BR-84 NO DATA NO DATA NO DATA LR-85 NO DATA NO DATA NO DATA . NO DATA 6.47E+08 NO DATA NO DATA NO DATA 6.77E+07 4 RB-86 NO DATA 1.05E+09 4.21E-47 8.59E-46 5.97E-46 NO DATA NO DATA NO DATA RB-88 NO DATA 1.46E-55 1.67E-53 1.49E-53 NO DATA NO DATA NO DATA RB-89 NO DATA NO DATA 5.37E+08 NO DATA 3.96E+08 NO DATA NO DATA SR-89 1.39E+10 NO DATA NO DATA 3.16E+09 2.35E+11 NO DATA 5.95E+10 NO DATA gt-90 1.02E+04 NO DATA NO DATA NO DATA 5.99E+05 p t-91 2.71E+05 NO DATA 8.74E+01 i
NO DATA 1.85E-01 NO DATA NO DATA NO DATA SR-92 4.61E+00 NO DATA 1.10E+05 NO DATA 1.03E+00 NO DATA NO DATA Y-90 3.86E+01 NO DATA 6.73E-17 1.25E-21 NO DATA NO DATA Y-91m 3.44E-20 NO DATA NO DATA NO DATA 6.22E+05 Y-91 4.67E+03 NO DATA 1.25E+02 NO DATA 8.64E-07 NO DATA NO DATA NO DATA 8.73E-01 Y-92 3. 02 E-05 NO DATA 3.29E-03 NO DATA NO DATA NO DATA 1.79E+03 Y-93 1.20E-01 NO DATA 1.44E+02 NO DATA 1.05E+05 ERv95 4.58E+02 1.01E+02 8.97E+01 NO DATA 1.95E-02 NO DATA 4. 76E-02 NO DATA 5.02E+03 ER-97 2.29E-01 3.31E-02 2.75E+07 1.48E+04 1.06E+04 NO DATA 1.39E+04 NO DATA N4,-95 3.61E+04. 2.08E+07 NO DATA 8.05E+06 HO-99 NO DATA 9.74E+06 2.41E+06 NO DATA 5.13E+01 NO DATA 4.50E+01 1.57E+00 1.76E+03 TC-99m 1.58E+00 3.10E+00 1.61E-60 2.04E-59 NO DATA 2.74E-59 8.50E-61 5.11E-60 TC-101 1.54E-60 1.28E+03 NO DATA 1.32E+04 RU-103 5.10E+02 NO DATA 1.96E+02 NO DATA NO DATA 1.65E-04 NO DATA 3.99E-03 NO DATA 2.96E-01 RU-105 4.53E-04 NO DATA 1.72E+05 1.11E+04 NO DATA 1.38E+03 NO DATA 1.49E+04 RU-106 3.15E+07 NO DATA 2.01E+09 AG-110m 2.50E+07 1.69E+07 1.35E+07 NO DATA 1.18E+06 2.48E+06 NO DATA NO DATA 8.53E+06 TE-125m 8.84E+96 2.39E+06 2.96E+06 5.96E+06 7.10Et07 NO DATA 2.02E+07 TE-127m 2.49E+07 6.71E+06 1.39E+04 7.65E+01 2.47E+02 1.01E+03 NO DATA
.TE-127 3.57E+02 9.61E+01 3.96E+07 9.06E+06 5.03E+06 1.05E4 07 9.52E+07 NO DATA TE-129m 3.24E+07 9.55E-09 TE-129 1.53E-10 4.28E-11 3.64E-11 1.09E-10 4.49E-10 NO DATA 6.60E+04 7.02E+04 1.36E+05 6.39E+05 NO DATA 2.68E+06 TE-131m 1.91E+05 5.92E-33 NO DATA 1.03E-32 TE-131 1.96E-33 5.97E-34 5.83E-34 1.50E-33 i
.)
CLINTON-1 3-84 Rev.16-12/1
CPS-ODCM ~ TABLE 3.5-22 (continued) GOAT MILK PATHWAY FACTORS - R*.n (CHILD) 8 (m'm' rem /yr per pCi/sec) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE TE-132 1.23E+06 5.45E+05 6.59E+05 7.94E+05 5.06E+06 NO DATA 5.49E+06 I-130 2.06E+06 4.17E+06 2.15E+06 4.59E+08 6.23E+06 NO DATA 1.95E+06 I-131 1.56E+09 1.57E+09 8.94E+08 5.20E+11 2.58E+09 NO DATA 1.40E+08 I-132 8.32E-01 1.52E+00 7.03E-01 7.09E+01 2.34E+00 NO DATA 1.80E+00 I-133 2.06E+07 2.55E+07 9.64E+06 4.73E+09 4.25E+07 HO DATA 1.03E+07 I-134 9.51E-12 1.77E-11 8.13E-12 4.06E-10 2.70E-11 NO DATA 1.17E-11 1-135 6.53E+04 1.17E+05 5.56E+04 1.04E+07 1.80E+05 NO DATA 8.95E+04 CS-134 6. 7 6E+1
- A 11E+11 2.34E+10 NO DATA 3.44E+10 1.23E+10 5.98E+08 Cs-136 3.03E+0' ,13E+09 5.39E+09 NO DATA 4.44E+09- 6.62E+08 2.93E+08 C5-137 9. 65 E< 3E+10 1.36E+10 NO D.\TA 3.01E+10 ~ 1.00E+10 5.78E+08 CS-138 1.15E . 9E-22 1.10E-22 NO DATA 1.12E-22 1.21E-23 7.34E-23 BA-139 2.42E-Oi +
. 9E-11 7.01E-10 NO DATA 1.13E-11 7.59E-12 1.40E-06 BA-140 1.40E+07 1.22E+04 8.15E+05 NO DATA 3.98E+03 7.29E+03 7.07E+06 BA-141 2.34E-46 1.31E-49 7.62E-48 NO DATA 1.13E-49 7.70E-49 1.33E-46 BA-142 1.31E-80 7.32E-82 ]
9.44E-84 NO DATA 7.64E-84 5.55E-84 1.71E-82 ' LA-140 2.32E+00 8.12E-01 2.53E-01 NO DATA NO DATA NO DATA 2.26E+04 LA-142 9.85E-12 3.14E-12 9.83E-13 NO DATA NO DATA NO DATA 6.22E-07 CE-141 2.62E+03 1.31E+03 1.94E+02 NO DATA 5.73E+02 NO DATA 1.63E+06. CE-143 2.24E+01 1.22E+04 1.76E+00 NO DATA 5.10E+00 NO DATA 1.78E+05' 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 9.29E+04 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 r187 3.46E+03 2.05E+03 9.20E+02 NO DATA NO DATA NO DATA 2.88E+05 .&-239 2.07E+00 1.49E-01 1.04E-01 NO DATA 4.29E-01 NO DATA 1.10E+04
- mrem /yr per pCi/m'
- 1.07 x-10' 4
CLINTON-1 3-05 Rev.16-12/97
CPS-ODCM TABLE 3.5-23 GOAT HILK PATHWAY FACTORS - Rh (TEEN) (m# mrem /yr per pCi) i LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ORGAN: BONE ISOTOPE NO DATA 2. 0 2 E+ 0 3
- 2.02E+03* 2.02E+03* 2.02E+03* 2.02E+03* 2.02E+03*
H-3 1.34E+05* 1.34E+05* C-14 6.70E+05* 1. 3 4 E+ 05
- 1.34E405* 1.34E+05* 1.34E+05*
5.15E+05** 5.15E+05 5.15E+05 5.15E+05 5.15E+05 5.15E+05 .5.15E+05 NA-24 3.18E+09 2.34E+09 1. 4 7 E+ 09 NO DATA NO DATA NO DATA P-32 3.78E+10 8.40E+03 9.98E+05 CR-51 NO DATA NO DATA 5.94E+03 3.30E+03 1.30E+03 1.68E+06 3.32E+05 NO DATA 5.00E+05 NO DATA 3.44E+06 "' HN-54 NO DATA 8.77E-04 1.56E-04 NO DATA 1.11E-03 NO DATA 5.77E-02 HH-56 NO DATA 4.11E+05 9.57E+04 NO DATA NO DATA 2.60E+05 1.78E+05 FE-55 5.79E+05 4.97E+05 3.73E+06 FE-59 6.75E+05 1.58E+06 6.08E+05 NO DATA NO DATA 9.51E+05 2.19E+06 NO DATA NO DATA NO DATA 1.31E+07 CO-58 NO DATA 3.32E+06 7.47E+06 NO DATA NO DATA NO DATA 4.32E+07 CO-60 NO DATA 1.60E+07 1.00E+08 4.81E+07 NO DATA NO DATA NO DATA NI-63 1.42E+09 1.03E-02 4.71E-03 NO DATA NO DATA NO DATA 5.61E-01 NI-65 0.09E 02 3.63E+05 4.68E+03 2.20E+03 NO DATA 1.18E+04 NO DATA CU-64 NO DATA 2.52E408 8.76E+08 4.09E+08 NO DATA 5.61E+08 NO DATA 3.71E+08 ZN-65 ZN-69 4.44E-13 8.46E-13 5.92E-14 NO DATA 5.53E-13 NO DATA 1.56E-12 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA ER-83 NO DATA NO DATA NO DATA-FR-84 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA BR-85 NO DATA 8.38E+07 5.66E+08 2.66E+08 HO DATA NO DATA NO DATA RB-86 NO DATA 3.99E-53 NO DATA 4.66E-46 2.48E-46 NO DATA NO DATA NO DATA RB-8 8 - 9.52E-54 6.73E-54 NO DATA NO DATA NO DATA 1.46E-62 RB-89 NO DATA 5.59E+09 NO DATA 1.60E+08 NO DATA NO DATA NO DATA 6.65E+08 SR-89 3.87E+09 1.38E411 NO DATA 3.40E+10 NO DATA NO DATA NO DATA t-90 NO DATA 5.01E+05 X-91 1.11E+05 NO DATA 4.40E+03 NO DATA NO DATA 1.89E+00 NO DATA 8.0$E-02 NO DATA NO DATA NO DATA 4.81E+01 SR-92 1.29E+05 Y-90 1.56E+01 NO DATA 4.21E-01 NO DATA NO DATA NO DATA 5.37E-22 NO DATA NO DATA NO DATA 6.64E-19 Y-91m 1.41E-20 NO DATA 7.75E+05 Y-91 1.89E+03 NO DATA 5.07E+01 NO DATA NO DATA NO DATA 3.57E-07 NO DATA Hu DATA NO DATA 3.39E-01 Y-92 1.23E-05 NO DATA 4.86E-02 NO DATA 1.33E-03 NO DATA NO DATA NO DATA 1.49E+03 Y-93 1.44E+05 err-95 1.98E+02 6. 2 4 E+ 01 4.29E+01 NO DATA 9.17E+01 NO DATA ZR-97 9.43E-02 1.87E-02 8.60E-03 NO DATA 2.83E-02 NO DATA 5.05E+03 I N -95 1.69E+04 9.37E+03 5.16E+03 NO DATA 9.08E+03 NO DATA 4.01E+07 HO-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 2.4BE+01 NO DATA 2.86E+01 1.06E+00 1.26E+03 TC-101 6.26E-61 8.91E-61 8.~l5E-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 NO DATA 2.35E-03 NO DATA 1.50E-01 RU-106 4.47E+03 NO DATA- 5.63E+02 NO DATA 8.62E+03 NO DATA 2.14E+05 AG-110m 1.15E+07 1.09E+07 6.62E+06 NO DATA 2.00E+07 NO DATA 3.06E+09 TT-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 4.00E+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 HO DATA 4.94E+07 TE-129 6.22E-11 2.32E-11 1.51E-11 4.44E-11 2.61E-10 NO DATA 3.4OE-10 TE-131m 7.86E+04 3 . 7 'I E+ 04 3.14E+04 5.67E+04 3.93E+05 NO DATA 3.02E+06 TE-131 8.04E-34 3.31E-34 2.51E-34. 6.19E-34 3.51E-33 NO DATA 6.60E-35
~CLINTON-1 3-86 Rev.16-12/@
CPS-ODCM - TABLE 3.5-23 (continued) , C GOAT MILK PATHWAY FACTORS - R ,n (TEEN)
? (m* mrem /yr per pCi/sec) -
ORGAN: BONE LIVER T.DODY THYROID KIDNEY LUNG GI-LLI ISOTOPE 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 2.00E+08 3.93E406 NO DATA 1.96E+06 I-131 6.44E+08 9.01E+08 4.84E+08 2.63E+11 1.55E+09 NO DATA 1.78E+08 I-132 3.52E-01 9.20E-01 3.30E-01 3.10E+01 1.45E+00 NO DATA 4.01E-01 I-133 8.48E+06 1.44E407 4.39E+06 2.01E+09 2.52E+07 HO DATA 1.09E+97 I-134 4.03E-12 1.07E-11 3.04E-12 1.78E-10 1.68E-11 NO DATA 1.41E-13 1-135 2.75E+04 7.00E+04 2.62E+04 4.56E+06 1.12E+05 NO DATA 7.05E+04 CS-134 2.94E+10 6.91E+10 3.21E+10 NO DATA 2.20E+10 8.39E+09 8.60E+08 CS-136 1.34E+09 5.27E+09 3.54E+09 NO DATA 2.87E+09 4.52E+06 4.24E+08 CS-137 4.01E+10 5.33E+10 1.86E+10 NO DATA 1.82E+10 7.05E+09 7.59E+08 CS-138 4.73E-23 9.08E-23 4.54E-23 NO DATA 6.70E-23 7.80E-24 4.12E-26 BA-139 9.84E-09 6.92E-12 2.87E-10 NO DATA 6.53E-12 4.77E-12 8,78E-08 BA-140 5.82f+06 7.13E+03 3.75E+05 NO DATA 2.42E+03 4.80E+03 8 98E+06 BA-141 9.53E?47 7.11E-50 3.18E-48 NO DATA 6.60E-50 4.87E-50 2,03E-52 BA-142 5.44E-81 5.44E-84 3.35E-82 NO DATA 4.60E-84 3.62E-84 1,67E-92 LA-140 9.67E-01 4.75E-01 1.26E-01 HO DATA NO DATA NO DATA 2.73E+04 LA-142 4.08E-12 1.81E-12 4.51E-13 NO DATA NO DATA NO DATA 5.52E-08 CE-141 1.07E+03 7.12E+02 8.17E+01 NO DATA 3.35E+02 NO DATA 2.04E+06' CE-143 9.14E+00 6.65E+03 7.43E-01 NO DATA 2.98E+00 NO DATA 2.00E+05-CE-144 7.86E+04 3.25E+04 4.23E+03 NO DATA 1.94E+04 NO DATA 1.98E+07 PR-143 3.47E+01 1.39E+01, 1.73E+00 NO DATA 8.06E+00 NO DATA 1.14E+05 PR-144 1.42E-54 5.81E-55 7.19E-56 NO DATA 3.33E-55 NO DATA 1.56E-57 ND-147 2.17E+01 2.36E+01 1.41E+00 NO DATA 1.38E+01 NO DATA 8.50E+04 yl87 1.43E+03 1.16E+03 4.08E+02 NO DATA NO DATA NO DATA 3.15E+05
..P-239 8.38E-01 7.90E-02 4.39E-02 NO DATA 2.40E-01 NO DATA 1.27E+04 cmrem/yr per pCi/m 3 6 **5.15 x.10 CLINTON-1 3-87 Rev.16-12/9~1
3dS-OG3H 1VEI'3 C
- S-E D i
DOVI HIIP> dV1liMVA 3V31OUS - U% )VGOI'l( i, )m,maam/ AJ daJ 1 TDT / sac ( I'I A3H 1 G00A 1HAUOIG MIGN3A I'nND DI-ITI OUDVN: GON3 Is01Od3 f H-E NO QVIV I*SS3+0E. I*SS3+0E. I*SS3+00 I*SS3+0E, I*G93+0E. I*SS3+0E. L*E93+0t, t*Z93+0t. L*Z93+0te t*Z93+ot. L*393+09, L*Z93+0t. f 3-ID E'9E3+0S+ Z*6S3+OS,, Z*6S3+OS Z*6S3+OS Z*693+OS Z*6S3+OS Z*6S3+OS 'Z*653+0S "NV-Zt Z*0S3+IO I'ZL3+06 L*613+08 NO GVIV HO GVIV NO OVIV Z*E03+06 d-EZ 3U-SI NO GYIV NO QVIV E*tE3+0E Z*0S3+0E L*993+OZ )*993+0C 8*9E3+OS NO QVIV I*OI3+09 I*6Z34OS NO GVIV Z*663+OS NO QVIV E*083+09 HN-SP HN-59 NO QVIV t*693-09 8*t63-0S NO GY1V 9'Z63-09 NO QVIV I'983-OZ E'ZL3+OS E'Z93+OS S'ZL3+09 NO QVIV NO OVIV I*E93+OS~ I*E03+OS 33-SG E*0Z3+09' E'8S3+OG 6*093+OS C*tL3+09 NO GY1V NO GVIV Z*SE3+OS J3-96 30-99 NO UVIV S'9Z3+OS I'Z93+09 NO QVIV NO GVIV NO QVIV I*It3+OL L y 30-90 NO GVIV I*693+09 t*EE3+09 NO QVIV NO W1V NO GVIV E'963+OL MI-9E 8*OS3+08 9*983+OL Z*L03+OL NO QVIV NO GY1V NO UY1V I*I93+04 NI-9S t*tE3-02 S*t93-0E Z*9E3-0E NO QVIV NO GY1V NO QVIV I*t93-01 3n-9) NO QVIV Z*9Z3+0E I*ZE3+0E NO OVIV 9'9Z3+0E NO UY1V Z*Z)3+0S S'Z33+08 Z*E93+09 NO UY1V E*t63+08 NO QVIV E*Z63+08 2N-99 I'9t3+08 2N-96 Z*tI3-IE t'913-IC E'ZI3-ID NO QVIV C*003-IE NO QVIV 9*6E3-IP l NO GY1V NO QVIV NO GVIV NO OVIV NO GVIV NO OVIV NO QVIV 2U-SE NO QVIV ' HH-8P NO GVIV NO GMIV NO GVIV NO QVIV NO GVIV 'NO GYIV . NO GVIV NO OVIV .NO GVIV NO QVIV NO GVIV NO QVIV NO GVIV EH-8S HH-89 NO W1V C*I03+08 I*PG3+08 NO QVIV NO QVIV NO QVIV 9*1Z3+0L HH-88 NO QVIV Z*SL3-t9 I*E93-t9 NO QVIV NO GVIV NO GVIV E*SS3-SL ME-86 NO GM1V S*Ct3-SD E't83-S> NO QVIV NO GVIV NO GV1Y C*IE3-9L SU-86 C*093+06 NO OVIV 8*LE3+OL NO QVIV NO GVIV NO GVIV )*883+08 6*483+IO NO QVIV Z*t03+IO NO01V NO GVIV NO QVIV Z*8E3+06 4-60
-61 9'013+0t NO GVIV Z*>E3+0E NO QVIV NO GVIV NO GY1V Z*893+0S SH-6Z I*0E3+00 NO GY1V t*)S3-0Z NO QVIV NO GVIV MO QVIV Z*0t3+01 A-60 8*t83+00 NO QVIV Z*393-01 NO GVIV NO QVIV NO QVIV 6*003+09 1-6IW L*963-ZI NO QVIV Z*683-ZZ NO QVIV NO GVIV NO QVIV Z*393-ZO A-61 I*0E3+0E NO GY1V Z*LS3+01 NO QVIV NO QVIV NO QVIV S'993+OS A-6Z 9'983-09 NO GVIV I*6S3-OL NO QVIV NO QVIV NO GY1V I*IL3-01 1-GE Z*993-OZ NO GVIV L*EZ3-09 NO QVIV NO GVIV NO QVIV 8*tI3+OZ 2H-6S I*IE3+02 E'9E3+01 Z*t93+01 NO QVIV S'963+OI NO GY1V I 1G3+05 2H-6L S*IE3-OZ I*093-OZ t *Lt3-OE NO GY1V I*S83-OZ NO GY1V E'ZE3+OE N"-6S 6*603+0E S*SI3+0E Z*693+0E NO QVIV G*tS3+0E NO QVIV E*E)3+OL HC-66 NO GVIV Z*693+09 S'9E3+OS NO QVIV 9*LI3+09 NO GY1V 9*893+09 13-66M E*6S3-OI I*IZ3+00 I*)Z3+OI NO QVIV I*L03+OI S*tL3-01 9*9I3+02 13-I01 E*DE3-91 D*6D3-91 t*9t3-90 NO GVIV 8*863-90 Z*SZ3-91 I*t83-LZ un-10E I*333+0Z NO QVIV S*2)3+OI NO QVIV t*993+OZ NO QVIV I*)Z3+OP Hn-IOS I*OZ3-09 NO QVIV )*0Z3-0S NO QVIV I*EE3-OE NO QVIV 9'ZE3-02 un-109 Z*tt3+0E NO OVIV C*063+OZ NO QVIV t*LE3+0E NO QVIV I*583+OS YD-1105 9*693+09 9*t93+09 E'8Z3+09 NO GVIV I'Zt3+OL NO QVIV Z*9E3+06 s3-Igsm I*653+09 L*OL3+OS 'Z*9I3+OS S*8L3+OS L*6t3+09 NO QVIV L*L63+09 13.tgLm G*t93+09 I*6S3+09 9*993+0S I*t03+09 Z*333+OL NO QVIV Z*8E3+OL 13-IZL L*8Z3+01 Z*8I3+01 I'963+OI 9 803+01 E*163+02 NO GY1V 9*It3+OE 13-IE6M E'Z13+09 Z*963+09 I*I)3+09 Z*983+09 E*OI3+OL NO GVIV E'9E3+OL 13-IZ6 E'8E3-II I*Et3-II 8'ZC3-IZ Z*G63-II I*tZ3-IO NO GVIV Z*GS3-II 13-IEIm )*EE3+0D Z'IZ3+0D I*t93+0D E*ES3+09 Z*It3+OS NO QVIV Z*103+09 13-IEI )*EL3-EP I'8E3-CD I*C83-ED E'903-ED I*6Z3-EE NO GVIV 9'I63-ES l
(. l l m mm-L c-su ua^'I9-IE/6[
l I CPS-ODCM . TABLE 3.5-24 (continued) , GOAT MILK PATHWAY FACTORS - R".g (ADULT)
/ (m' mrem /yr per pCi/sec) .
ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE 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 > -I-131 3.54E+08 5.06E+08 2.90E408 1.66E+11 8.68E+08 NO DATA 1.34E+08 I-132 1.98E-01 5.29E-01 1.85E-01 1.85E+01 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 I-134 2.27E+12 6.16E-12 2.20E-12 1.07E-10~ 9.80E-12 NO DATA 5.37E-15 I-135 1.55E+04 4.06E+04 1.50E+04 2.68E+06 6.51E+04 NO DATA 4.59E+04 C5-134 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 C3-138 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 3.54E-12 2.15E-12 9.4AE-09 i 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 DATA 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 4.2SE-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 1.82E+02 NO DATA 1.50E+06 . CE-143 5.00E+00 3.70E+03 4.09E-01 No DATA 1.63E+00 NO DATA 1.38E+05 CE-144 4.29E+04 1.79E+04 2.30E+03 NO DATA 1.06E+04 NO DATA 1.45E+07 PR-143 1.89E+01 7.56E+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 i ND-147 1.13E+01 1.30E+01 7.79E-01 NO DATA 7.64E+00 NO DATA 6.25E+04 1187 7.78E+02 6.50E+02 2.27E+02 NO DATA NO DATA NO DATA 2.13E+05 . eP-239 4.39E-01 4.32E-02 2.38E-02 NO DATA 1.35E-01 NO DATA 8.86E+03 -
*mrtm/yr per 5
Ci/m'
**2.95 x 10 ,
i l l l CLINTON-1 3-09 Rev.16-12/97
CPS-ODCM TABLE 3.5-2_5 ; HEAT PATHWAY FACTORS - R".y (CHILD) g) (m# mrem /yr per pCi/sec) T. BODY -THYROID KIDNEY LUNG GI-LLI ORGAN: BONE LIVER ISOTOPE NO DATA 2.33E+02* 2.33E+02* 2.33E+02* 2.33E+02* 2.33E+02* 2.33E+02* H-3 1.06E+05* 1.06E+05* C-14 5.29E+05* 1.06E+05* 1.06E+05* 1.06E+05* 1.06E+05* 1.84E-03** 1.84E-03 1.84E-03 1.84E-03 1.84E-03 1.84E-03 1.84E-03 .NA-24 2.05E+08 7.43E+09 3.47E+08 2.86E+08 NO DATA NO DATA NO DATA P-32 8.90E+03 4.66E+05 CR-51 No DATA NO DATA 8.78E+03 4.88E+03 1.33E+03 No DATA 8.03E+06 2.14E+06 NO DATA 2.25E+06 NO DATA 6.74E+06 MN-54 NO DATA 1.56E-53 3.52E-54 NO DATA 1.89E-53 NO DATA 2.26E-51 MN-56 4.50E+07 FE-55 4.58E+08 2.43E+08 7.52E+07 NO DATA NO DATA 1.37E+08 3.76E+08 6.09E+08 3.03E+08 NO DATA NO DATA 1.76E+08 6.34E+08 FE-59 NO DATA 1.64E+07 5.03E+07 NO DATA NO DATA NO DATA 9.58E+07 CO-58 CO-60 NO DATA 6.93E+07 2.04E+08 NO DATA NO DATA NO DATA 3.84E+08 2.91E+10 1.56E+09 9.90E+08 NO DATA NO' DATA ' NO DATA 1.05E+08 NI-63 4.10E-51 NI-65 3.$5E*52 - ~ 3. 3'4E 53~ ' 1. 92Er-53~ NO* DATA NO DATA NO DATA CU-64 No DATA 2.775-07 1.67E-07 NO DATA 6.69E-07 No DATA 1.30E-05 EM 3.75E408 1.00E+09 6.22E+08 NO DATA 6.30E+08 NO DATA 1.76E+08 EM-69 0.00E+00 'O.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 NO DATA CR-83 NO DATA NO DATA - CR-84 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA BR-85 RS-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 ' RS-89 NO DATA 0.00E+00 0.00E+00 NO DATA NO hATA NO DATA 0.00E+00 SR-89 4.80E+08 NO DATA 1.37E+07 NO DATA NO DATA NO DATA 1.86E+07 y-90 1.04E+10 NO DATA 2.64E+09 NO DATA NO DATA NO DATA 1.40E+08 2.26E-10 NO DATA 8.535-12 NO DATA NO DATA NO DATA 4.99E-10
'hd-91 SR-92 2.00E 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 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-12 NO DATA 1.92E-13 NO DATA NO DATA NO DATA 1.04E-07 ER-95 2.67E+06 5.87E+05 5.22E+05 NO DATA 8.40E+05 NO DATA 6.12E+08 ER-97 3.16E-05 4. 5'J E-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 HO-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 5.90i!;-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 l
RU-106 4.43E+09 NO DATA 5.53E+08 NO DATA 5.99E+09 NO DATA 6.90E+10 AG-110m 8.41E+06 5.68E+06 4.54E+06 NO DATA 1.06E+07 NO DATA 6.75E408 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 HO 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. *l 9 E+ 09 4.99E+08 2.77E+08 5. *16E+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. 5*1 E+ 02 4.96E402 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 t CLINTON-1 3-90 Rev.16-12/9h
CPS-ODCM . TABLE 3.5-25 (continued) , MEAT PATHWAY FACTORS - R",y (CHILD)
' (m' mrem /yr per pci/sec)
ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE 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 ')6 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 1-132 1.05E-58 1.93E-58 8.06E-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 1-134 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 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 1.88E+08 NO DATA 4.15E+08 1.49E+08 7.98E+06 C5-138 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 0.00E400 NO DATA 0.00E+00 0.00E+00 0.00E+00 BA-140 4.38E+07 3.84E+04 2.56E+06 NO DATA 1.25E+04 2.29E+04 2.22E+07 BA-141 0.00Ef00 0.00E+00 0. 00E4 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 6.0$E-03 NO DATA NO DATA NO DATA 5.41E+02 LA-142 6.18E-92 1.97E-92 6.17E-93 NO DATA NO DATA NO DATA 3.91E-87 , CE-141 2.22E+04 1.11E+04 1.64E+03 NO DATA 4.85E+03 NO DATA 1.38E+07 . 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 PO DATA 1.89E+08 PR-143' 3.34E+04 1.00E+04 1.66E+03 NO DATA 5.45E+03 NO DATA 3.60E+07 PR-144 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 NO DATA 0.00E+00 ND-147 1.17E+04 9.47E+03 7.33E+02 NO DATA 5.20E+03 NO DATA 1.50E+07
)-187 3.21E-02 1.90E-02 8.53E-03 NO DATA NO DATA NO DATA 2.67E+00
- AP-239 4.23E-01 3.04E-02 2.14E-02 NO DATA 8.79E-02 NO DATA 2.25E+03
- mrem /yr per pCi/m'
**1.84 x 10-'
~
)
I i 1 l i I
)
.CLINTON-1 3-91 Rev.16-12/97
C PS-ODCM TABLE 3.5-26 MEAT PATHWAY FACTORS - R".y (TEEN) it (r.* mrem /yr per Ci) ORGAN: DONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE H-3 NO DATA 1.93E+02* 1.93E+02* 1.93E+02* 1.93E+02* 1.93E+02* 1.93E+02* C-14 2.81E+05* 5.62E+04* 5.62E+04* 5.62E+04* 5.62E+04* 5.62E+04* 5.62E+04* HA-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+0C 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 FZ-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+38 NO DATA NO DATA 1.56E+08 1.17E+09 CO-58 NO DATA 1.41E+07 3.25E+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 NI-63 1.52E+10 1.07E+09 5.15E+08 NO DATA NO DATA NO DATA 1.71E+08 NI-65 1.90E;52 2.43E-53 1.11E-53 NO DATA NO DATA No DATA 1.32E-51 CU-64 NO DA'[A 2.06E-07 9.68E-08 NO DATA 5.21E-07 NO DATA 1.60E-05 ZN-65 2.50E+08 8.69E+0B 4.05E+0B NO DATA 5.56E+08 NO DATA 3.68E+08 EN-69 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 NO DATA 0.00E+00 ER-83 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA FR-84 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA. aR-85 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA RB-86 NO 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+b0 0.00E+00 NO DATA NO DATA NO DATA 0.00E+00 SR-89 2.54E+08 NO DATA 7.27E+06 NO DATA NO DATA NO DATA 3.02E+07 g y-90 3.04E+09 NO DATA 1.99E+09 NO DATA NO DATA NO DATA 2.26E+08 1A-91 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-40 Y-90 9.11E+01 NO DATA 2.45E+00 NO DATA NO DATA NO DATA 7.51E+05 Y-91m 0.00E+00 NO DATA 0.00E+00 NO DATA NO DATA NO DATA 0.00E+00 Y-91 9.55E+05 NO DATA 2.56E+04 NO DATA NO DATA NO DATA 3.91E+08 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 1.13E-07 ZRr95 1.50E+06 4.74E+05 3.25E+05 NO DATA 6.93E+05 NO DATA 1.09E+09 ZR-97 1.70E-05 3.36E-06 1.55E-0G 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 6.26E-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 RU-106 2.36E+09 NO DATA 2.97E+08 NO DATA 4.54E+09 NO DATA 1.13E+11 AG-110m 5.04E+06 4.77E+06 2.90E+06 NO DATA 9.10E+06 NO DATA 1.34E+09 TE-125m 3.03E+08 1.09E+08 4.06E+07 8.47E+07 NO DATA NO DATA 8.95E+08 TE-127m 9.40E+08 3.33E+08 1.12E+08 2.24E+08 3.81E+09 NO DATA 2.34E+09 TE-127 1.78E-10 6.3CE-11 3.82E-11 1.23E-10 7.20E-10 NO DATA 1.37E-08 TE-129m 9.49F+08 3.52E+08 1.50E+08 3.06E+08 3.97E+09 NO DATA 3.56E+09 TE-129 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00F,+00 TE-131m 3.73E+02 1.79E+02 1.49E+02 2.69E+02 1.87E+03 NO DATA 1.44E+04 TE-131 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00
)
CLINTON-1 3-92 Rev.16-12/97
C PS -ODCM - TABLE 3.5-26 (continued) MEAT PATilWAY FACTORS - R".y (TEEN)
) (m# mrem /yr per pCi/sec) j ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE ]
TE-132 1.17E+06 7.3BE+05 6.95E+05 7.78E+05 7.00E+06 NO DATA 2.34E+07 l I-130 1.63E-06 4.71E-06 1.88E-06 3.84E-04 7.25E-06 NO DATA 3.62E-06 Ie131 8.89E+06 1.24E+07 6.69E+06 3.63E+09 2.14E+07 NO DATA 2.46E+06 I-132 5.78E-59 1.51E-50 5.42E-59 5.09E-57 2.38E-50 NO DATA 6.58E-59 . I-133 3.09E-01 5.25E-01 1.60E-01 7.32E+01 9.20E+01 NO DATA 3.97E-01 1-134 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0. G'0 E+00 NO DATA 0.00E+00 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+0B 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 0.00Ef00 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 1.49E-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 . 55 E- 8 8 - 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 3.04E+05 NO DATA 3.10E+08 PR-143 1. *J 7 E+ 04 7.06E+03 0.80E+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 ,%-187 1.74E-02 1.42E-02 4.96E-03 NO DATA NO DATA NO DATA 3.83E+00 '#P-239 2.25E-01 2.12E-02 1.18E-02 NO DATA 6.67E-02 NO DATA 3.42E+03 {
*mrcm/yr per pCi/m' *
- 1.16 x 10-8 l l
n CLINTON-1 3-93 Rev.16-12/97
CPS-ODCM TABLE 3.5-27 ) MEAT PATHWAY FACTORS - R".y (ADULT) iI (m# mrem /yr per pCi/sec)
~
ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE H-3 NO DATA 3.24E+02* 3.24E+02* 3.24E+02* 3.24E+02* 3.24E+02* 3.24E+02* C-14 3.33E+05* 6.66E+04* 6.66E+04* 6.66E+0(* 6.66E+04* 6.66E+04* 6.66E+04*' NA-24 1.45E-03** 1.45E-03 1.45E-03 1.45E-03 1.45E-03 1.45E-03 1.45E-03 P-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 HN-54 NO DATA 9.19E+06 1.75E+06 NO DATA 2. 7 3 E+ 0 6 NO DATA 2.81E+07 MN-56 NO DATA 1.45E-53 2.57E-54 NO DATA 1.84E-53 'HO DATA 4.62E-52 FE-55 2.94E+08 2.03E+08 4.74E+07 NO DATA NO DATA 1.13E+08 1.17E+08 FE-59 2.66E+08 6.24E+08 2.39E+08 NO DATA NO DATA
- 1.74E+08 2.08E+09 CO-58 NO DATA 1.83E+07 4.09E+07 NO DATA NO DATA NO DATA 3.70E+08 Co-60 NO DATA 7.51E+07 1.66E+08 NO DATA NO DATA NO DATA 1.41E+09 NI-63 1.89E+10 1.31E+09 6.32E+08 NO DATA NO DATA NO DATA 2.73E+08 NI-65 2.27E%2 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 ZN-65 3.56Ef08 1.13E+09 5.12E+08 NO DATA 7.57E+08 NO DATA 7.13E+08 )
ZN-69 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 NO DATA 0.00E+00 ER-83 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA PR-84 NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA NO DATA LR-85 NO DATA- NO 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-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 l GR-89 3.01E+08; NO DATA 8.64E+06 NO DATA NO DATA NO DATA 4.83E+07 JiR-90 1.24E+10 NO DATA 3.05E+09 NO DATA NO DATA NO DATA 3.59E+08 [h-91 1.43E-10 NO DATA 5.79E-12 NO DATA NO DATA NO DATA 6.83E-10 l SR-92 1.28E-49 NO DATA 5.54E-51 NO DATA 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 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-0G 1.88E-06 NO DATA 6.17E-06 NO DATA 1.27E+00 l N -95 2.30E+06 1.28E+06 6.86E+05 NO DATA 1.26E+06 NO DATA 7.75E+09 HO-99 NO DATA 9.91E+04 1.89E+04 NO DATA 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 RU-105 5.42E-28 NO DATA 2.14E-28 NO DATA 7. 0 0E-27 NO DATA 3.32E-25 RU-106 2.81E+09 NO DATA 3.55E+08 NO DATA 5.42E+09 NO DATA 1.82E+11 AG-110m 6.67E+06 6.17E+06 3.67E+06 NO DATA 1.21E+07 HO DATA 2.52E+09 TE-125m 3.59E+08 1.30E+08 4.81E+07 1.00E+08 1.46E+09 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
)
l CLINTON-1 3-94 Rev.16-12/97 1 1
CPS-ODCM .
. TABLE 3.5-27 (continued) .
MEAT PATHWAY FACTORS - R"m - (ADULT) '8 1 (m' mrem /yr per pCi/sec) <
. (
ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE 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-5/ 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 1-134 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 NO DATA 0.00E+00 1-135 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 1.55Ef09 1.27E+09 NO DATA 5.03E+08 1.67E+08 2.72E+0/
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 l BA-139 0.00E+00- 0.00E+00 0.00E+00 NO DATA 0.00E+00 0.00E+00 0.00E+00 l BA-140 2.88E+07 3.62E+04 1.89E+06 NO DATA 1.23E+04 2.07E+04 5.94E+07 BA-141 0.00(+00 0.00E+00 0.00E+00 WO 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 3.68E-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 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 0.00E+00 0.00E+00. NO DATA 0.00E+00 NO DATA 0.00E+00 ND-147 7.04E+03 8.14E+03 4.87E+02 NO DATA 4.76E+03 NO CATA 3.91E+07 4 .187 2.06E-02 1.72E-02 6.02E-03' NO DATA NO DATA NO DATA 5.64E+00 NP-239 2.57E-01 2.53E-02 1.39E-02 NO DATA 7.88E-02 NO DATA 5.18E+03 {'
- mrem /yr per pCi/m'
*
- 1. 4 5 x 10-'
e ( _ CLINTON-1 3-95 Rev.16-12/97
3 dS-OC3H IVaI'3 c
- S-28 A3931V1 ION dV1liMVA 3V31OUS - M(O )3llII'O(
)m,maam/42 daa froT/ sac (
I'IA3H 1*G00A 1HAUOIG MIGN3A I'nND DI-ITI OUDVN3 GON3 I SDI.od3 P*OI3+OE* H-E NO GVIV )*OI3+0E. >*OI3+0E. )*0I3+0E. t*OI3+0E. t*OI3+OE. L*OI3+05 L*OI3+OS. L*OI3+OS. L*OI3+OS. L*OI3+OS. L*OI3+09 ,3-IP C*SI3+09 C*LS3+OS E*LS3+OS E'LS3+OS.. E*LS3+0S E*LS3+OS E*LS3+OS E*LS3+OS NV-Zt NO OVIV 6*C03+OL d-CZ E*EL3+06 I*SL3+03 I*E03+00 NO QVIV NO QVIV NO QVIV NO GVIV I*It3+OS 9*t63+09 I'LL3+ot I*T03+OS 9'Z03+09 38-51 I*093+00 NO QVIV S*S03+08 HN-SP NO UVIV 9*9t3+00 I*LL3+00 NO QVIV I*Bt3+OI t'ZZ3+00 NO QVIV E'Z93+01 NO QVIV Z*LI3+OE HN-99 NO GVIV L*893+0L j O*OZ3+00 t*ZG3+08 I*EZ3+00 NO QVIV NO QVIV Z*>03+08 J3-SS I*BL3+08 9*L03+00 33-S6 C*683+00 9*tE3+08 E*ZI3+09 NO UVIV NO UVIV 9*tt3+OL I*6L3+09 NO OVIV NO UVIV NO UY1V E'L93+08 30-SG NO QVIV Z*T03+06 E*t63+08 I*IZ3+06 NO QVIV NO QVIV NO UVIV 30-90 NO UY1V I*)Z3+09 NI-9E .E*6S34IO Z*II3+06 I*Et3+06 NO UY1V NO MY NO UVIV 6*963+00 S*Lt3+00 NO QVIV NO QVIV NO GVIV I*213+OE NI-9S I*053+0Z NO UY1V S*IE3+09 3n-9F NO UV.JV I*063+ot 9*963+0E NO UY1V Z*973+09 Z*193+06- I*Et3+06 NO OVIV I*E93+06 NO UY1V E'L63+00 2N-9S 8*I'I3+08 I*2)3-09 NO GVIV 8*193-09 NO QVIV 8*t93-09 2N-96 6*Z63-09 I*Et3-0S NO UY1V NO GVIV EH-8E NO MY NO MV S*)03+00 MO QVIV NO QVIV NO UVIV E*633-II NO UY1V NO UVIV MO QVIV NO UY1V - GH-8P NO UVIV NO UVIV NO MV NO UVIV - NO QVIV NO mV NO QVIV EH-SS NO UVIV NO QVIV Z*6I3+OL UE-89 NO 0viV t*SE3+00 Z*L63+09 NO QVIV NO QVIV t E83-ZZ C*OP3-ZZ NO GY1V NO QVIV MO QVIV Z'IS3-ZE B8-88 NO UV1Y NO QV1Y )*063-Z9 NO UVIV t*963-Z9 t*IL3-29 HO QVIV NO QVIV HG-96 NO QV.TY I*E63+06 SH-06 E'S63+IO NO UY1V I*0E3+06 NO QVIV NO QVIV NO UY1V E*It3+II NO GVIV NO UYIV HO UY1V I'9L3+TO SU-60 I*Et3+IZ NO QVIV I*6L3+09 NO QVIV NO GVIV NO GYIV I*IS3+09 fH-61 S*213+OS NO QVIV NO QVIV I*E83+OP SH-6Z L*Z63+02 NO QVIV Z*6Z3+01 NO QVIV 9*193+OZ NO QVIV NO QVIV NO QVIV 9*S03+OL A-60 Z*EI3+09 NO QVIV NO GY1V C*E93-IO NO QVIV NO QVIV NO OVIV I'913-0S X-6IW 6*Et3-06 Z >93+06 NO QVIV >*6L3+OS NO QVIV NO QVIV NO QVIV A-6I I*893+04 NO QVIV )*SL3+OP A-6Z I*S03+00 NO QVIV t'S33-OZ NO UV1Y NO QVIV NO QVIV 8*0I3+00 NO GY1V NO GVIV NO QVIV t*ES3+09 A-6E Z*6Z3+OZ 8*893+00 E*893+09 8*t63+OS t*593+OS NO QVIV I'Z23+09 NO QVIV 2846S I'Z)3+OL 3H-6L S'993+02 8*183+01 )*8E3+01 NO QVIV I*It3+OZ NO GY1V I'903+OS I*It3+OS- NO QVIV I*S03+OS NO OVIV Z*6S3+08 M#-6S )*T03+OS 9*ES3+09 NO QVIV L*9L3+09 I*603+09 NO QVIV I*9)3+OL NO QVIV HO-66 )*993+00 S*Z)3+OE 13-66W )*L03+00 6*ZI3+00 I*SE3+0Z NO QVIV I*E)3+02 NO GVIV Z*9E3-Z6 0*t93-EI t*6I3-EO 13-IOI I*t02-EO I'993-EO I*693-Z6 NO GY1V E*6L3+08 un-I0E I
- S t 3+ OL NO QVIV S*603+09 NO QVIV C*093+OL NO GVIV C*EZ3+01 NO QVIV 9*093+0Z NO QVIV S*683+09 Hn-IOS 6'I93+OI NO GVIV 6*E03+OL NO QVIV I*013+06 NO OVIV I*193+IO 30-109 L*t93+09 NO OVIV Z*983+06 VD-IIOW E'ZI3+OL Z*It3+OL I*LE3+OL NO QVIV t*073+OL 6*S23+OL t'903+OL 6*893+OL NO QVIV NO GY1V E*E63+00 13-Iggm C*SI3+00 I*OL3+06 E'993+08 I*St3+08 C*I93+08 E'LL3+06 NO OVIV 13-IZLm I*E23+06 NO GY1V C*093+OS 13-IZL 6*093+0E Z*953+0E Z*II3+0E 9*BI3+0E Z*003+09 Z*ES3+08 I*EI3+00 Z*L23+00 Z*tL3+05 NO GVIV I*0E3+06 13-IE6m 0*tE3+00 0*213-02 E'993-06 C*IE3-09 6*tZ3-09 C*993-OE NO GY1V 13-126 I*E23-OE NO GVIV Z*193+OL 13-IEIW I*St3+09 S*EE3+OS S'9L3+OS I*I03+09 S*t93+09 L*LI3-19 I*603-IS L*0E3-IS NO QVIV I*E93-IP 13-ICI Z*S63-IS L*863-I9 3I' INION-I C-69 BaA*I9-I2/61
l CPS-ODCM - TABLE 3.5-20 (continued) . VEGETATION PATHWAY FACTORS - R\n (CHILD) (m* mrem /yr per pCi/sec) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI 8SOTOPE TE-132 7.00E+06 3.10E+06 3.74E+06 4.51E+06 ~ 2.88E+07 NO DATA 3.12E+07 8-130 6.10E+05 1.23E+06 6.35E+05 1.36E+08 1.84E+06 NO DATA 5.77E+05
- I2.131 1.43E+08 1.44E+08 8.16E+07 4.75E+10 2.36E+08 NO DATA l '. 2 B E+ 07 I-132 9.20E+01 1.69E+02 7.77E+01 7.84E+03 2.59E+02 NO DATA 1.99E+02 I-133 3.53E+06 4.36E+06 1.65E+06 8.11E+08 7.27E+06 NO DATA 1.76E+06 I-134 1.50E-04 2.79E-04 1.28E-04 6.41E-03 4.26E-04 NO DATA 1.85E-04 I-135 6.28E+04 1.13E+05 5.34E+04 1.00E+07 1.73E+05 NO DATA B.61E+04 i 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 1.44E-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 2.40EE21 1.14E-24 6.64E-23 NO DATA 9.88E-25 6.71E-24 1.16E-21 5.65E-42 4.11E-42
~
BA-142 9.70E-39 6.98E-42 5.42E-40 NO DATA 1.27E-40 IA-140 3.24E+03 1.13E+03 3.53E+02 NO DATA NO DATA NO DATA 3.16E+07 IA-142 '3.39E-04 1.08E-04 3.38E-05 NO DATA NO DATA NO DATA 2.1$E+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 NO DATA 9.22E-27 NO DATA 3.75E-23 ND-147 7.161!;+04 5.80E+04 4.49E+03 NO DATA 3.18E+04 NO DATA 9.18E+07
;f-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/m'
**3.75 x 10' I
l l 4 k .. CLINTON-1 3-97 Rev.16-12/97
3dG-OG3H 1V873 C*9-26 A3D31V1 ION dVIHMVA 3V31 OHS - U% )133N(
)m,mlam/42 daa lioT( /OHDVNi HON 3 I'IA3H 1*GOGA 1HAHOIG MIGN3A I'nND DI-ITI IS01Od3 H-E NO OVIV Z*963+0E, Z*963+0E, Z*S63+0E, Z*963+0E* Z*S63+OE, Z*S63+0E, 3-IP I*t53+09, Z*613+OS, Z*6I3+09, Z*613+OS, Z*613+OS* Z*6I3+OS, Z*6I3+0S, NV-ZP Z*t03+OS,, Z*t03+OS Z*t03+OS Z*t03+OS Z*t03+0S Z*t03+OS Z*t03+OS d-EZ I'913+06 6*6L3+OL 9*Et2+OL NO QVIV NO OVIV NO QVIV .T
- ES3+09 3H-SI NO QVIV NO QVIV 9*I33+0t E't03+09 I*Et3+0t 9*Lt3+0t I*0E3+OL NN-SP NO QVIV )*St3+00 6*OI3+OL NO UVIV I*E93+09 NO QVIV 6*EE3+09 NN-99 NO UVIV I*tE2+OI Z*St2+00 NO MY I*9T2+01 NO QVIV 6*tI3+0E JE-SS E'Z93+09 Z*ET2+09 S*E62+OL NO UviV NO uviV I*t92+09 I*003+09 22-Sit I'L63+09 t*193+08 I'912+09 NO UVIV NO UviV I*EZ3+09 6*983+09 30-99 NO aviV t*E92+OL I*0T2+09 NO UM&Y NO UV4V NO 0vZV 9*0Z2+09
- 30-90 NO U41V ~Z*)62+09 S*902+09 NO UM1V NO UV1V NO UVIV E*E>2+06 NI-9E I'912+IO I*It2+06 S*t93+09 NO MY NO UW1V NO QVIV I"9T2+09 NI-95 G*.fE2+01 L*EE2+00" E*EP2+00- NO MY NO av&Y NO UVIV C*6L2+0E j
Dn-9P NO 041V 8'Z02+0E E*602+0E NO MV Z*t02+09 NO UVIV 9*tZ2+OS 2N-95 )*ZE2+09 I*tL2+06 9*993+09 NO M Y 6*tI2+09 NO M Y 9'ZE2+09 2N-96 S*092-09 6*902 9*LZ2-OL NO UV4V 9'Z93-09 NO UVIV I*LL2-09 3H-9E NO UVIV NO UV4V Z*6E2+00 NO MY NO 041V NO QVIV NO GM1V 3H-9P NO UVIV NO UM4V Z*tI2-II NO* M Y NO UM4V NO M Y NO UVIV 2U-99 NO UVIV NO M V NO MV NO M Y NO UVIV NO UVIV NO UV&V.- HS-99 NO UV1V Z*LZ2+08 I'Z93+09 NO MY NO 044V NO QVIV )*0Z2+0E HS-99 NO UV4V E*IL2-ZZ I'962-ZZ NO MY NO MY NO UY&Y Z*LZ3-Z6 H2-06 NO MY E'992-Z9 Z*932-Z9 NO MY NO UM&V NO UVZY S*t92-ES eh-96 I*St2+IO NO UM&V )*EE2+09 NO MY NO UVIV NO UVIV I'902+06 (-60 L*S02+11 NO UVIV I 953+11 NO UW4V NO QV&Y
~
NO UVIV Z*I12+10 l '$H-61 Z*9Z2+OS NO UM3V I*IZ2+09 NO M Y NO UM1V NO QVIV I'Z02+09 yfH-6Z )*002+0Z NO UY1V I'L02+01 NO MY NO OVIV NO QVIV I*033+09
/A-60 I*ES3+OP NO UY1V E*Et3+0Z NO MY NO UVIV NO QVIV I*0E3+09 A-6IW S*0t2-06 NO,OVIV I*6E3-IO NO MY NO UV4V NO UVIV Z*E82-OL A-61 L*S)2+09 NO uviV Z*T03+OS NO UVIV NO UVIV NO UY1V E'ZI3+06 A-6Z 9*903-0I NO OVIV Z*t62-0Z NO UMIV NO QVIV NO QVIV Z*E92+07 A-6E I'593+OZ NO OVIV )*Et3+00 NO M Y NO OVIV NO UV1Y t'9E2+09 2H-6S I*LE2+09 S*t93+OS C*LS3+OS NO UVIV 9*0Z3+OS NO GVIV I'Z93+06 28-6L E*103+0Z 9*It3+OI Z*9E2+01 NO UVIV 6*EI3+01 NO QVIV I'992+OL N*-6S I*6Z3+OS I*OL3+OS S'993+09 NO MV I*0E3+OS NO QVIV t'992+09 HO-66 NO UV1V S'993+09 I*093+09 NO UVZY I'Z63+OL NO QVIV I*OI3+OL 43-668 Z*LE3+00 L*9I3+00 -6*992+01 NO UVIV I*IE2+0Z t*ZE3+00 S 002+0E 43-I01 9*0Z2-EI I*It3-EO I*IZ3-36 NO QVIV Z*093-Z6 9*6S3-EI I*6S3-EL un-10E 9'9I2+09 NO GVIV Z*6I3+09 NO UVIV Z*t03+OL NO GY1V 9*963+09 un-I0S t*6L3+01 NO GV1Y I*6E3+OI NO QVIV 9'ZL3+02 NO QVIV t*OI3+0t un-109 C*063+09 NO GV1Y E'963+OL NO UVIV S*691+09 NO GVIV I*t93+IO VS-IIOW I*SI3+OL I*)E3+OL 9*LZ3+09 NO QVIV Z*LZ3+OL NO GY1V >*0E3+06 42-1Z98 I*t63+09 S'ES3+OL I*663+OL t*IS3+OL NO OVIV NO 0vlY )*E93+09 42-IELm S*Sg3+08 I*693+09 9*SL2+OL I*EI3+09 Z'Z)3+06 NO OVIV I*E93+06
&2-IZL S*L03+0E I*6Z3+OE I*t93+0E E*LE3+0E Z'I63+09 NO QVIV )*It3+OS 42-IZ6W T 903+08 I*Et3+09 S*L03+OL I*193+08 I*SI3+06 NO GY1V I*ES3+06 42-IZ6 L*IE3-07 Z*993-0t I*LE3-09 S*063-09 Z*663-0E NO GVIV C*603-0E 42-IEIW 8*tt3+0S >*053+OS E*E03+OS 9*063+OS >*Z23+09 NO QVIV E'ZS3+OL 43-ICI I*tI3-IS S*003-19 )*E63-19 I*093-IS 9*IS3-IS NO QVIV I*IS3-19 I
I l. DI' INION-I C-68 BaA*19-IE/6I l
1 CPS-ODCM . TABLE 3.5-29 (continued) . VEGETATION PATHWAY FACTORS - R*.y (TEEN) (m' mrem /yr per pCi/sec) /~
\
ORGAN: DONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE TE-132 3.91E+06 2.48E+06 2.33E+06 2.61E+06 2.37E+07 NO DATA 7.84E+07 I-130 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 3.13E+10 1.BSE+08 NO DATA 2.12E+07 I-132 5.19E+01 1.36E+02 4.87E+01 4.58E+03 2.14E+02 NO DATA 5.91E+01 I-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 I-135 3.53E+04 9.09E+04 3.37E+04 5.85E+06 1.44E+05 NO DATA 1.01E+05 CS-134 7.10E+09 1.67E+10 7.75E+09 NO DATA 5.31E+09 2.03E+09 2.08E+08 CS-136 4.37E+07 1.72E+08 1.16E+08 NO DATA 9.37E+07 1.48E+07 1.38E+07 CS-137 1.01E+10 1.35E+10 4.70E+09 NO DATA 4.59E+09 1.78E+09 1.92E+08 CS-138 3.54E-11 6.80E-11 3.40E-11 NO DATA 5.02E-11 5.84E-32 3.08E-14 BA-139 2.70E-02 1.90E-05 7.86E-04 NO DATA 1.79E-05 1. 31E 2.41E-01 BA-140 1.38E+08 1.69E+05 8.89E+06 NO DATA 5.73E+04 1.14E+05 2.13E+08 BA-141 1.11E-21 8.27E-25 3.70E-23 NO DATA 7.67E-25 5.66E-25 2.36E-27 BA-142 5.35E-39 5.35E-42 3.29E-40 NO DATA 4.53E-42 3.56E-42 1.64E-50 LA-140 1.80E+03 0.86E+02 2.36E+02 NO DATA NO DATA NO DATA 5.09E+07 IA-142 1.88E-04 8.35E-05 2.08E-05 NO DATA NO DATA NO DATA 2.54E+00 CE-141 2.83E+05 1.89E+05 2.17E+04 NO DATA 8.90E+04 NO DATA 5.41E+08' CE-143 9.33E+02 6.79E+05 7.58E+01 NO DATA 3.04E+02 NO DATA 2.04E+07 CE-144 5.29E+07 2.19E+07 2.84E+06 NO DATA 1.31E+07 NO DATA 1.33E+10 PR-143 7.00E+04 2.79E+04 3.40E+03 NO DATA 1.62E+04 NO DATA 2.30E+08 PR-144 3.04E-26 1.24E-26 1.54E-27 NO DATA 7.14E-27 NO DATA 3.35E-29 MD-147 3.62E+04 3.94E+04 2.36E+03 NO DATA 2.31E+04 NO DATA 1.42E+08 1187 3.53E+04 2.88E+04 1.01E+04 NO DATA NO DATA NO DATA 7.79E+06 dP-239 1.39E+03 1.31E+02 7.26E+01 NO DATA 4.10E+02 NO DATA 2.10E+07
$ mrem /yr per pCi/m' 5 **2.40 x 10 )
k._
@LINTON-1 3-99 Rev.16-12/97 l
9 CPS-ODCM TABLE 3.5-30 VEGETATION PATHWAY FACTORS - Rh (ADULT) i (m# mrem /yr per pCi/sec) ORGAN: BONE LIVER T. BODY THYROID KIDNEY LUNG GI-LLI ISOTOPE H-3 NO DATA 2.26E+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+05* 1.79E+05* 1.79E+05* 1.79E+05* NA-24 2.71E+05** 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+08 , 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 5.96E+07 NO DATA 9.30E+07 NO DATA 9.58E+08 HN-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 EN-65 3.18E+08 1.01E+09 4.57E+08 NO DATA 6.76E+08 NO DATA 6.36E+0'8 EN-69 5.39E-06 1.03E-05 7.17E-07 NO DATA 6.69E-06 NO DATA 1.555-06 ER-83 NO DATA NO DATA 3.13E+00 NO DATA NO DATA NO DATA 4.50E+00 ER NO DATA NO DATA 2.54E-11 NO DATA NO DATA NO DATA 1.99E-16.* LR-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-88 NO DATA' 3.43E-22 1.82E-22 NO DATA NO DATA NO DATA 4.74E-33 RB-89 NO DATA 3.96E-26 2.79E-26 NO DATA NO DATA NO DATA 2.30E-39
*R-89 9.95E+09 NO DATA 2.86E+08 NO DATA NO DATA NO DATA 1.60E+09 A-90 6.04E+11 NO DATA 1.48E+11 NO DATA NO DATA No DATA 1.75E+10 kR-91 3.02E+05 NO DATA 1.22E+04 NO DATA NO DATA NO DATA 1.44E+06 i
JR-92 4.28E+02 NO DATA 1.85E+01 NO DATA NO DATA NO DATA 8.48E+03 j_ Y-90 1.33E+04 NO DATA 3.56E+02 NO DATA NO DATA NO DATA 1.41E+08 Y-91m 5.42E-09 NO DATA 2.10E-10 NO DATA NO DATA NO DATA 1.59E-08 Y-91 5.12E+06 NO DATA 1.37E+05 NO DATA NO DATA NO DATA 2.82E+09 Y-92 9.13E-01 NO DATA 2.67E-02 NO DATA NO DATA NO DATA 1.60E+04 Y-93 1.69E+02 NO DATA 4.65E+00 NO DATA NO DATA NO DATA 5.35E+06 err 95 1.18E+06 3.79E+05 2.56E+05 NO DATA 5.94E+05 NO DATA 1.20E+09 ER-97 3.36E+02 6.78E+01 3.10E+01 NO DATA 1.02E+02 NO DATA 2.10E+07 N4-95 1.42E+05 7.91E+04 4.25E+04 NO DATA 7.82E+04 NO DATA 4.80E+08 MO-99 NO DATA 6.12E+06 1.16E+06 NO DATA 1.39E+07 NO DATA 1.42E+07 3.09E+00 TC-99m 8.73E+00 1.11E+02 NO DATA 1.33E+02 4.28E+00 5.16E+03 TC-101 8.62E-31 1.24E-30 1.22E-29 NO DATA 2.24E-29 6.35E-31 3.73E-42 RU-103 4.77E+06 NO DATA 2.06E+06 NO DATA 1.82E+07 NO DATA 5.57E+08 RU-105 5.36E+01 NO DATA 2.12E+01 NO DATA 6.93E+02 NO DATA 3.28E+04 RU-106 1.93E+08 NO DATA 2.44E+07 NO DATA 3.73E+08 NO DATA 1.25E+10 AG-110m 1.05E+07 9.75E+06 5.79E+06 ,NO DATA 1.92E+07 NO DATA 3.98E+09 TE-125m 9.67E+07 3.51E+07 1.30E+07 2.91E+07 3.93E+08 NO DATA 3.86E+08 TE-127m 3.49E+08 1.25E+08 4.26E+07 8.93E+07 1.42E+09 NO DATA 1.17E+09 TE-127 5.65E+03 2.03E+03 1.22E+03 4.19E+03 2.30E+04 NO DATA 4.46E+05 TE-129m 2.512+08 9.35E+07 3.97E+07 8.61E+07 1.05E+09 NO DATA 1.26E+09 TE-129 7.61E-04 2.86E-04 1.85E-04 5.84E-04 3.20E-03 NO DATA 5.75E-04 TE-131m 9.12E+05 4.46E+05 3.72E+05 7.06E+05 4.52E+06 NO DATA 4.43E+07 TE-131 1.51E-15 6.32E-16 4.78E-16 1.24E-15 6.63E-15 NO DATA 2.14E-16 i /
.)
CLINTON-1 3-100 Rev.16-12/97
CPS-ODCM
- TABLE 3.5-30 (continued)
VEGETATION PATHWAY FACTORS - R*.y (ADULT) (m* mrem /yr per pCi/sec) < ORGAN: DONE LIVER T. BODY TilYROID KIDNEY LUNG GI-LLI
- ISOTOPE TE-132 4.31E+06 2.79E+06 2.62E+06 3.00E+06 2.68E+07 NO DATA 1.32E+08 I-130 3.91E+05 1.15E+06 4.55E+05 9.77E+07 1.80E+06 NO DATA 9.93E+05 1-131 8.07E+07 1.15E+08 6.62E+07 3.78E+10 1.9BE+08 NO DATA 3.05Et07
- I-132 5.77E+01 1.54E+02 5.40E+01 5.40E+03 2.46E+02 NO DATA 2.90E+01
'I-133 2.09E+06 3.63E+06 1.11E+06 5.34E+08 6.34E+06 NO DATA 3.26E+06 'I-134' 9.33E-05 2.53E-04 9.06E-05 4.39E-03 4.03E-04 NO DATA 2.12E-07
- I-135 3.91E+04 1.02E+05 3.77E+04 6. 7 5E+ 06 1.64E+05 NO DATA 1.16E+05
- CS-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
- C -137 6.36E+09 8.70E+09 5.70E+09 NO DATA 2.95E+09 9.82E+08 1.68E+0B
.CS-130 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 1.91E-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 lBA-142 5.795-39 5.96E-42 3.64E-40 NO DATA 5.03E-42 3.37E-42 8.I6E-57 ,LA-140 1.98E+03 9.95E+02 2.63E+02 NO DATA NO DATA NO DATA 7.31E+07 lLA-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 lCE-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 NO DATA 8.14E+06 NO DATA 1.11E+10
'PR-143 6.26E+04 2.51E+04 3.10E+03 NO DATA 1.45E+04 NO DATA 2.74E+08 lPR-144 3.25E-26 1.35E-26 1.65E-27 .NO DATA 7.61E-27 NO DATA 4.68E-33 i'8D-147 3.33E+04 3.85E+04 2.31E+03 NO DATA 2.25E+04 NO DATA 1.85E+08 t F187 3.80E+04 3.18E+04 1.11E+04 NO DATA NO DATA NO DATA 1.40E+07 lNP-239 1.43E+03 1.40E+02 7.74E+01 NO DATA 4.38E+02 NO DATA 2.88E+07
*mrcm/yr per5 pCi/m' **2.71 x 10 i
I l 1 l l 1
)
CLINTON-1 3-101 Rev.16-12/97
I l l l CPS-ODCM TABLE 3.5-31 J GROUND PLANE PATilWAY FACTORS - R 3 i (m' mrem /yr per pCi/sec) l l l . l TOTAL TOTAL TOTAL ISOTOPE BODY SKIN ISOTOPE BODY SKIN ISOTOPE BODY SKIN H-3 0.00E+00 0.00E+00 Y-91 1.07E+06 1.21E+06 CS-136 1.51E+08 1.71E+08 i l l 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 4.10E+05 l l
l P-32 0.00E+00 0.00E+00 ZR-95 2.45E+08 2.85E+08 BA-139 1.06E+05 1.19E+05 CR-51 4.65E+06 5.50E+06 ZR-97 2.96E+06 3.44E+06 EA-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 1 l MN-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' O.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 *C-101 2.03E+04 2.26E+04 LA-142 7.60E+05 9.12E+05 CO-58 3.00E+08 4.45E+08 RU-103 1.08E+0B 1.26E+08 CE-141 1.37E+07 1.54E+07-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 NI-65 2.97E+05 3.45E+05' AG-110m 3.4 4E+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 1.84E+03 2.11E+03 ZN-65 7.48E408 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 FR-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 4.99E+06 RD-89 1.23E+05 1.48E+05 I-130 5.50E+06 6.68E+06 CR-89 2.16E+04 2.50E+04 I-131 1.72E+07 2.09E+07
. .- 9 0 NO DATA NO DATA I-132 1.25E+06 1. 47E4 06 R-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 5.31EdO3 I-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' i
l l l 1 CLINTON-1 3-102 Rev.16-12/97
' CPS-ODCM .
4.0, COMPLIANCE WITH 40CFR190 , 4.1 Total Dose - Operation and Surveillance Requirements
.lDPERATION REQUIREME'T N The' annual (calendar year) . dose or dose commitment to any MEH3ER OF THE PUBLIC due to releases of radioactivity and to radiation from uranium fuel cycle cources 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 mrem. This - requirement is applicable at all times. REMEDIAL REQUIREMENT:
.a. With the calculated doses from the release of 4 radioactive materials in liquid or gaseous effluents exceeding twice the limits of Sections 2.4.1(a)*.,
- 2. 4.1 (b) , 3. 5.1 (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 outside storage tanks to determine whether the above limits of Section 4.1 have been exceeded.
If such is the case, prepare 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 (2 s releases to prevent recurrence of exceeding the i above limits and. includes the schedule for achieving conformance with the above limits. This Special Report, as defined in 10CFR20 Part 2203(4), 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.
i
.2. A determination of the maximum exposed individual. ~
L l
) -
(v CLINTON-1 4-1 Rev.16-12/97
CPS-ODCM
- 3. A determination of the total annual dose to the maximum exposed individual from all existing pathways and sources of radioactivity and j' 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 methodology or measured.#
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 40CFR Part 190 has not already
- & been corrected, the Special Report shall
- include a request for a variance in accordance with the provisions of 40CFR Part 190.
Submittal of the report is considered a timely request, and a variance is granted until staff action on the request is complete. SURVEILLANCE REQUIREMENTS 4.1.1 Cumulative dose contributions from liquid and gaseous effluents 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 manual.
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).
#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 d,uring the previous three quarters and from the quarter in which the Section 4.1 OPERATION REQUIREMENT was exceeded.
CLINTON-1 - 4-2' Rev.16-12/97
CPS-ODCM ' 5.0 RADIOLOGICAL ENVIRONMENTAI, MONITORING PROGRAM The primary requirements for the Clinton Power Station Radiological Environmental Monitoring Program (REMP) are - l set forth in Table 5.1-1 and shown by location in Figures I 5.0-1, 5.0-2, 5.0-3 and 5.0-4. In addition to the required sampling program, CPS will perfona supplemental periodic and long term sampling and analyses in order to better monitor environmental exposure pathways. These samples will not be listed in this manual, however, full salaple descriptions and results will be included in the Annual Radiological Environmental Operating Report. Surface and drinking water samples are composited by l I collecting aliquots of fixed volume at fixed time Aintervals. This method of sampling is considered
,-consistent with note (g) in Table 5.1-1.
5.1 Monitoring Program - Operation and Surveillance j Requirements i l OPERATION REQUIREMENT The Radiological Environmental Monitoring Program shall be conducted as specified in Table 5.1-1. This , requirement applies at all times. . l l REMEDIAL REQUIREMENT:
- 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 ,
reguired by Technical Specification 5.6.2, a description of the reasons for not conducting the program as required and the plans for preventing a recurrence.
)
CLINTON-1 5-1 Rev.16-12/97
, CPS-ODCM l
- b. With the level of radioactivity as the result of plant effluents in an environmen.tal sampling medium at a specified location exceeding the report levels of Table 5.1-2 when averaged over any calendar
)
I quarter prepare and submit to the Regional Administrator of the Regional Office of the NRC l within 30 days a Special Report that Adentifies the l cause(s) for exceeding the limit (s) and defines the I corrective actions to be taken to reduce radioactive ! ef fluents so that the potential annual dose' ..to a MEMBER OF THE PUBLIC is less than the calendar year l 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 submitted if: concentration (1) + concentration (2) + ~>1.0
. # reporting. level (1) reporting le' vel (2)
? l When radionuclides other than those in Table 5.1-2 are detected and the result of plant effluents, this report shall be submitted if the potential annual , l 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 effluents; however, in such an event, the condition shall be reported and
) described in the Annual Radiological Environmental Operating Report.
- c. With milk or fresh leafy vegetation samples unavailable from one or more of the sample locations required by Table 5.1-1, identify locations for
- obtaining replacement samples and add them to the radiological environmental monitoring program within 30 days. The specific locations from which samples were unavailable may then be deleted from the monitoring program. Pursuant to Technical l Specification 5.6.2, identify the cause of the
'The methodology and parameters used to estimate the potential annual dose to a MEMBER OF THE PUBLIC shall be indicated in this report.
t CLINTON-1 5-2 Rev.16- 12 / 9*/
CPS-ODCM
' unavailability of samples and identify the new loca tion (s) for obtaining replacement samples in the next annual Radiological Environmental Operating Report and also include in the report a revised
' figure (s) and~ table for this manual reflecting the 4 new location (s).
SURVEILLANCE REQUIREMENTS 5.1.1 The radiological environmental monitoring samples shall be collected pursuant to Table 5.1-1 from the specific locations given in Table 5.1-1 and Figures 5.0-1, 5.0-3, and 5.0-4 and shall be analyzed pursuant to5.0-2, the j requirements of Table 5.1-1 and the detection I capabilities required by Table 5.1-3. l I 1 1 (
' )
I ) CLINTON-1 5-3 Rev.16-12/97
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)
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CPS-ODCM TABLE 5.1-1 (Continued) RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM , .\ ! l I , TABLE NOTATIONS l
- Refer to NUREG-0133, " Preparation of Radiological Effluent
- Technical Specifications for Nuclear Power Plants," October 1978, and to Radiological Assessment Branch Technical Position,
( Revision 1, November 1979. Deviations are permitted from.the required sampling schedule if specimens are unobtainable due to hazardous conditions, seasonal unavailability, malfunction of automatic sampling equipment and other legitimate reasons. If l specimens are unobtainable due to sampling equipment i malfunction, every effort shall be made to complete corrective action prior to the end of the next sampling period. All deviations from the sampling schedule shall be documented in the ' AnnualsRadiological Environmental Operating Report pursuant to Technical Specification 5.6.2. It is recognized that, at times, l l it may'not be possible or practicable to continue to obtain samples of the media of choice at the most desired location or , time. In these instances suitable alternative media and locations may be chosen for the particular pathway in question and appropriate substitutions made within 30 days in the i radiological environmental monitoring program. Pursuant to Technical Specification S.6.2, identify the cause of the unavailability of samples for that pathway and identify the new gI location (s) for obtaining replacement samples in the next annual
/ Radiological Environmental Operating Report and also include in the report a revised figure (s) and table for the ODCM reflecting !
the new location (s). b one or more instruments, such as a pressurized ion chamber, for measuring and recording dose rate continuously may be used in
- place of, or in addition to, integrating dosimeters. For the purposes of this table, a thermoluminescent dosimeter (TLD) is considered to be one phosphor; two or more phosphors in a packet are considered as two or more dosimeters. Film badges shall not be used as dosimeters for measuring direct radiation. The 40 stations is not an absolute number. The number of direct radiation monitoring stations may be reduced according to geographical limitations; e.g., at an ocean site, some sectors l
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.
)
CLINTON-1 5-14 Rev.16-12/97
C PS-ODCM TABLE 5.1-1 (Continued) , RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM TABLE NOTATIONS (Continued)
"The purpose of this sample is to obtain background information.
If it is not practical.to establish control locations in accordance with the distance and wind direction criteria,,other i sites that provide valid background data may be substituted. d Airborne particulate sample filters shall be analyzed for gross beta radioactivity 24 hours or more after sampling to allow for t radon and thoron daughter decay. If grass 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.
' Gamma isotopic analysis means the identification and quantification of gamma-emitting radionuclides that may be i
attributable to the effluents from the facility. .
'The " upstream sample" shall be taken at a distance beyond significant influence.of the discharge. The " downstream" sample shall be taken in an area beyond but near the mixing zone.
" Upstream" samples in an estuary must be taken far enough l! upstream to be beyond the plant influence. Salt water shall be sampled only when the receiving water is utilized for recreational activities.
[
'A composite sample is one in which the quantity (aliquot) of liquid sampled is proportional to the quantity of flowing liquid * (or time) and in which the method of sampling employed results in j a sp'ecimen 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 j
compositing period (e.g., monthly) in order to assure obtaining a representative sample.
" 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.
'The dose shall be calculated for the maximum organ and age j group, using the methodology and parameters in Section 2.4.2. j i
CLINTON-1 5-15 Rev.16-12/97
C PS-ODCM TABLE 5.1-1 (Continued) RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM
'i' .
TABLE NOTATIONS (Continued)
'If harvest occurs more than once a year, sampling shall be {
performed during each discrete harvest. If harvest occurs Attention shall be paid continuously, sampling shall be monthly. to including samples of tuberous and root food products.
"The dose shall be calculated for the maximum organ and age group, using the methodology and parameters in Section 3.5.4.
. a
)
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CLINTON-1 5-16 Rev.16-12/97
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CPS-ODCM ~ TABLE 5.1-3 (Continued) , DETECTION FOR ENVIRONMENTAL SAMPLE ANALYSIS **"
. TABLE NOTATIONS : "This list does not mean that only these nuclides are to be <
considered. Other peaks are identifiable, together with those of the above nuclides, shall also be analyzed and reported in the Annual Radiological Environmental Operating Report pursuant to Technical Specification 5.6.2.
" Required detection capabilities for thermoluminescent dosimeters used for environmental measurements shall be in accordance wit.h the recommendations of Regulatory Guide 4.13, Rev. 1, July 1977. *The LLD is defined, for purposes of these specifications, as the smallest concentration of radicactive material in a sample.that will yi, eld a net count, above system background, that will be detected with 95% probability with only 5% probability of f'lsely a concluding that a blank observation represents a "real" signal.
For a particular measurement system, which may include radiochemical separation: LLD = 4. 66s e / [E
- V
- 2.22
- Y
- exp (' lat) ) -
Where: ( LLD is the "a priori' lower limit of detection as defined above- as picocuries per unit mass or volume, se is the standard deviation of the background counting rate or of the counting rate of a blank sample as appro~priate, as counts per minute, E if the counting efficiency, as counts per disintegration, V is the sample size in units of mass or volume, 2.22 is the number of disintegrations per minute per picocurie, Y is the fractional radiochemical yield, when applicable, A is the radioactive decay constant for the particular radionuclide ( sec-* ) , and 1 ( CLINTON-1 5-19 Rev.16-12/97
C PS-ODCM At for environmental samples is the elapsed time between sample collection, or end of the sample collection period, and time of counting (sec).
-Typical values of E, V, Y, and At should be used in the j l
calculation. It should be recognized that the LLD is defined as an a priori (before the fact) limit representing the capability of a , measurement system and not as an a posteriori (after the fact) limit for a particular measurement. 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 Envitonkental Operating Report pursuant to Technical , 1 Specification 5.6.2. CLINTON-1 S-20 Rev.16-12/97
CPS-ODCM . 5.2 Land Use Census - Operation and Surveillance Requirements . OPERATION REQUIREMENT
,A land use census shall be conducted and shall identify
'within a distance of 8 km (5 miles) the location in each
( of the 16 meteorological sectors of the nearest milk animal, the nearest residence and the nearest garden
- of greater than 50 m2 (500 ft2) producing broad leaf vegetation. For evaluated or mixed-mode releases'as defined in Regulatory Guide 1.111, Revision 1, July 1977, {
J the land use census shall also identify within a distance of 5 km (3 miles) the location in each of the 16 meteorological sectors of all milk animals and all gardens of greater than 50 m2 producing broad leaf vegetation. This requirement applies at all times.
. AEMEDIAL REQUIREMENT:
- 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 new location (s) , in ' the next annual Radiological Environmental Operating Report, pursuant to Technical Specification 5.6.2.
- b. With a land use census identifying a location (s) that yields a calculated dose or dose commitment (via ths same exposure pathway) 20 percent greater (
than at a location from which samples are currently being obtained in accordance with 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 l or dose' commitment (s), via the same exposure I
- Broad leaf vegetation sampling of at least three i 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 i sampling in Table 5.1-1.4c shall be followed, including analysis of control samples. . CLINTON 1 5-21 Bev.16-12/97
C PS-ODCM
-pathway, may be deleted from this monitoring program after October 31 of the year in which this land use census was conducted. Pursuant to Technical
% Specification 5.6.3, identify the new location (s) in the next Radioactive Effluent Release Report and also include )
'in the report a revised figure (s) and table for this manual reflecting the new location (s), i SURVEILLANCE REQUIREMENTS 5*.2.1 The land use census shall be conducted during the growing season at least once per 12 months using that information that will provide the best results, such as by a door-to-door survey, aerial survey, or by consulting local agriculture authorities. The results of the land use census shall be included in the annual Radiological Environmental Operating Report pursuant to Technical
. iSpecification 5.6.2.
5.3 IInterlaboratory 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 has participated in interlaboratory comparison (cross-check) programs since
) the fonnulation.of its quality control program in 1 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 concentrations 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 specific ranges indicate a need to check the instruments or procedures used. r CLINTON-1 5-22 Rev.16-12/97
CPS-ODCM If the results of a determination in the EPA cross-check 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 correct it. The results of
,'this investigation and corrective action shall be f-(
' 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). 5.3.1 Interlaboratory Comparison Program - Operation and Surveillance Requirements i OPERATION REQUIREMENT 5 Analyses shall be performed 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.
REMEDIAL REQUIREMENT:
- a. With analyses not being performed as required above, report the corrective actions taken to prevent a recurrence to the Commission in the Annual Radiological Environmental Operating Report pursuant to Technical Specification 5.6.2. ( l SURVEILLANCE REQUIREMENTS 5.3.1.1 The Interlaboratory Comparison Program is described in l Section 5.3. A summary of the results obtained as part of the above required Interlaboratory Comparison Program shall be included in the Annual Radiological Environmental Operating Report pursuant to Technical" Specification 5.6.2.
l l (v CLINTON-I 5-23 Rev.16-12/97
CPS-ODCM FIGURE 5.0-1
. REMP LOCATIONS WITHIN 1 MILE OF CPS i
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l CPS-ODCM ' FIGURE 5.0-2 REMP LOCATIONS 1-2 HILES FROM CPS - g N
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C PS-ODCM FIGURE 5.0-3 REMP LOCATIONS 2-5 MILES FROM CPS i) e N
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CLINTON-1 5-26 Rev.16-12/97
CPS-ODCM FIGURE 5.0-4 REMP LOCATIONS GREATER THAN 5 MILES FROM CPS - -) , 1 l r-- , j K00PGHG1 % 74 % MORTON N
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09 ) CLINTON-1 5-27 Rev.16-12/97
CPS-ODCM 6.0 BASES FOR OPERATION AND SURVEILLANCE REQUIREMENTS 6.1 General Operation and Surveillance Requirements The requirements of. Sections 1.2 and 1.3 provide general tequirements 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 necessary to constitute compliance with the terms of an l' individual Operation Requirement and associated-REMEDIAL REQUIREMENT.
. i 1.3.1 This requirement provides that surveillance
' activities, necessary to ensure the Operation l Requirements are met, will be performed during the conditions for 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 tolerances for performing surveillance activities beyond those specified in the nominal surveillance interval. These tolerances 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 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. I CLINTON-1 6-1 Rev.16-12/97
CPS-ODCM . 1.3.3 The provisions of this requirement set forth the , I criteria for determination of compliance with the . OPERABILITY requirements of the Operation Requirements.
.Under these criteria, equipment, systems, or components -m l) i
~
,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 l
Requirements. 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 onda current basis as required to meet the OPERABILITY itequirements of the Operation Requirement.
Under the terms of this requirement, for example, during initial plant startup or following extended plant outage, the applicable surveillance activities must be performed within the stated surveillance interval prior to placing or returning the system or equipment into OPERABLE
- status.
I 6.2 Monitoring Instrumentation [ Section 2.7: Radioactive Liquid Effluent Monitoring Instrumentation The radioactive liquid effluent instrumentation is provided to monitor and control, as applicable, the releases of radioactive materials in liquid effluents during actual or potential releases of liquid effluents. The alarm / trip setpoints for these instruments shall be calculated and adjusted in accordance with the methodology an'd parameters in this manual to ensure that the alarm /t' rip will occur prior to exceeding the limits of 10CFR 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 10CFR Part 50. I CLINTON-1 6-2 Rev.16-12/97
1 I l' CPS-ODCM Section 3.9.1: Offgas Radiation Monitoring Instrumentation The OPERABILITY of the radiation monitoring
)) - instrumentation ensures that; (1) the radiation levels
^
tare 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 l consistent with 10CFR Part 50, Appendix A, General Design Criteria 19, 60, 61, 63 and 64. Section 3.9.2: Radioactive Gaseous Effluent Monitoring Instrumentation
.The radioactive gaseous effluent instrumentation is provided to monitor and control, as applicable, the Telease 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 I l the alarm / trip will occur prior to exceeding the limits l of 10CFR 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 l
-) 10CFR Part 50. The sensitivity of any noble gas activity monitors used to show compliance with the gaseous l
effluent release requirements of Section 3.5.1 shall be such that concentrations as low as 1 x 10-' pCi/ml are measurable. 6.3 Radioactive Effluents 6.3.1 Liquid Effluents Section 2.3.1: Liquid Effluent Concentration This requirement is provided to ensure that the , concentration of radioactive materials released in liquid waste effluents to UNRESTRICTED AREAS will be less than the concentration levels specified in 10CER Part 20, Appendix B, Table 2, Column 2. This limitation provides additional assurance that the levels of radioactive materials in bodies of water in UNRESTRICTED.' AREAS will result in exposures within (1) the Section II.A design objectives of Appendix I, 10CFR Part 50, to a MEMBER OF
\b i
i CLINTON-1 6-3 Rev.16-12/97 l
l CPS-ODCM l THE PUBLIC and (2) the limits of 10CFR Part 20.1301 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 lim in air
,(submersion) was converted to an equivalent concentration {'
, 'in water using the methods described in International i Commission on Radiological Protection (ICRP) Publication l
- 2. .
This requirement applies to the releas'e of radioactive , materials in liquid effluents from the site. ' The required detection capabilities for radioactive materials in liquid waste samples are tabulated in terms l 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:
- -iDefinition and Elaboration of a Proposed Position for 3
-Radiological Effluent and Environmental Measurements,"
'NUREG/CR-4007 (September 1984), and in the HASL Procedures Manual, HASL-300 (revised annually).
Section 2.4.1: 10CFR50, Appendix I Relea'se Rate Limits (
)
This requirement is provided to implement the requirements of Sections II.A, III.A and IV.A of Appendix I, 10CFR 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 set forth in Section IV.A of Appendix I to assure l that the releases of radioactive material in liquid effluents to UNRESTRICTED AREAS will be kept "as low as , is reasonably achievable." Also, for fresh water sites l with drinking water supplies that can be potentially l affected by plant operations, there is reasonable assurance that the operation of the facility will not result in radionuclide concentrations in the finished drinking water that are in excess of the requirements of 40CFR 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 based on models and data, such that the actual exposure of a MEMBER OF THE PUBLIC through appropriate pathways is unlikely to be substantially underestimated. .The
' equations specified in this manual for calculating the doses due to the actual release rates of radioactive materials in liquid effluents are consistent with the
) T CLINTON-1 6-4 Rev.16-12/97
1 CPS-ODCM 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 10CFR Part 50, Appendix I," Revision 1, i) pctober 1977 and Regulatory Guide 1.113, " Estimating Aquatic Dispersion of Effluents from Accidental and Routine Reactor Releases for the Purpose of Implementing Appendix I," April 1977.
This requirement applies to the release of radioactive materials in liquid ef fluents from the one reactor unit on the site. Section 2.5.1: Liquid 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 of radioactive materials in liquid effluents will be kept "as low as is reasonably achievable." This specification:
implements the requirements of 10CFR Part 50.36a, General Design Criterion 60 of Appendix A to 10CFR Part 50 and the design objective given in Section II.D of appendix I to 10CFR Part 50. The specified limits governing the use
),' of appropriate portions of the liquid radwaste treatment system were specified as a suitable fraction of the dose design objectives set forth in Section II.A of Appendix I, 10CFR Part 50, for liquid effluents. ,
This requirement applies to the release of radioactive materials in liquid effluents from the one reactor unit on the site. 6.3.2 Gaseous Effluents l Section 3.4.1: 10CFR20 Release Rate Limits This requirement is provided to ensure that the dose at l any time at and beyond the SITE BOUNDARY from gaseous effluents from all units on the site will be within the annual dose limits of 10CFR Part 20 to UNRESTRICTED I AREAS. The annual dose limits are the doses associated with the concentrations of 10CFR Part 20, Appendix B, Table 2, Column 1. These limits provide reasonable assurance that radioactive material discharged in gaseous effluents will not result in the exposure of a MEMBER OF hI CLINTON-1 6-5 Rev.16-12/97
C PS-ODCM ' THE PUBLIC in an UNRESTRICTED AREA, either within or , outside the SITE BOUNDARY, to annual average concentrations exceeding the limits specified in Appendix
. B, Table 2 of 10CFR Part 20. For MEMBERS OF THE PUBLIC
. pho may at times be :within the SITE BOUNDARY, the (-
o
' ccupancy of that MEMBER OF THE PUBLIC will usually be sufficiently low to compensate for any increase in the atmospheric diffusion factor above that for the SITE BOUNDARY. Examples of such MEMBERS OF THE PUBLIC, with the appropriate occupancy factors, shall be given in this manual. Doses for such MEMBERS OF THE PUBLIC are provided in the Radioactive Effluent Release Report. The specified release rate limits restrict, at all times, the corresponding gamma and beta dose rates above background to a MEMBER OF THE PUBLIC, at or b'eyond the SITE BOUNDARY, to less than or equal to 500 mrem / year to the I 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 dose rate above- J background to a child via the inhalation pathway to less than'or equal to 1500 mrem / year.
1 This requirement applies to the release of radioactive l materials in gaseous effluents from'the one reactor unit on the site. I i The required detection capabilities for radioactive materials in gaseous waste samples are tabulated in terms
)
of the lower limits of detection (LLDs). Detailed ( discussion of the LLD, and other detection limits can be found in 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 3.5.1: Noble Gas Dose This requirement is provided to implement the requirements of Sections II.B, III.A and IV.A of Appendix I, 10CFR Part 50. The 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 forth in Section IV.A of Appendix I to assure that the releases of radioactive material in gaseous
' effluents to UNRESTRICTED AREAS will be kept f'as low as is reasonably achievable." The Surveillance Requirements implement the requirements in Section III.A of Appendix I )
CLINTON-1 6-6 Rev.16-12/97
CPS-ODCM that conformance with the guides of Appendix I be shown
. by calculational procedures based on models and data such that the actual exposure of a MEMBER OF THE PUBLIC through appropriate pathways is unlikely to be
') -substantially underestimated. The dose calculation imethodology and parameters established in this manual for calculating the doses 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 Effluents for the Purpose of Evaluating Compliance with 10CFR Part 50, Appendix I,"
Revision 1, October 1977 and Regulatory Guide 1.111,
" Methods for Estimating Atmospheric Transport and Dispersion of Gaseous Effluents in Routine Releases from Light-Water Cooled Reactors" Revision 1, July 1977. The equations in this manual for determining the air doses at
,and beyond 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: Iodine-131, Iodine-133, Tritium, and { Radionuclides in Particulate Form This requirement is provided to implement the requirements of Sections II.C, III.A and IV.A of Appendix I, 10CFR Part 50.
--)3 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 material 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 10CFR Part 50, Appendix I," Revision 1, October 1977 and Regulatory
( .)> _ l CLINTON-1 6-7 Rev.16-12/97 l
C PS- ODCM . Guide 1.111, " Methods for Estimating Atmospheric , Transport and Dispersion of Gaseous Effluents in Routine Releases from Light-Water Cooled Reactors" Revision 1, July 1977. These equations also provide for determining (~
. lthe actual doses based upon the real time atmospheric (
' conditions. The release rate specifications for iodine-131, tritium, and radionuclides in particulate form with half lives greater than 8 days are dependent upon the existing radionuclide pathways to man in.the areas at and beyond the SITE BOUNDARY. The pathways that were examined in the development of these calculations were:
(1) individual inhalation of airborne radionuclides, (2) deposition of radionuclides onto green leafy vegetation with subsequent consumption by man, (3) deposition onto grassy areas where milk animals and meat producing animals graze with consumption of the milk and meat by
, man, and (4) deposition on the ground with subsequent
- iexposure of man.
This requirement applies to the release of. radioactive
~
materials in gaseous effluents from one reactor unit on the site. l Sections 3.6 and 3.7: Gaseous Radwaste (Offgas) Treatment { and Ventilation Exhaust Treatment System
- The OPERABILITY of the WASTE GAS HOLDUP SYSTEM and the
! VENTILATION EXHAUST TREATMENT SYSTEM ensures that the l systems will be available for use whenever gaseous ( l effluents require treatment prior to release to the l ! environment. The requirement that the appropriate portions of these systems be used, when specified, provides reasonable assurance'that the releases of r;adioactive materials in gaseous effluents will be kept "as low as reasonably achievable." This requirement implements the requirements of 10CFR Part 50.36a, General l -Design Criterion 60 of Appendix A to 10CFR Part 50 and the design objectives given in Section II.D of Appendix I J to 10CFR Part 50. The specified limits governing the use Q I 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, 10CFR Part 50, for gaseous effluents. This requirement applies to the release of radioactive materials in gaseous effluents from the one reactor unit on the site. l l . i ._ CLINTON-1 6-8 Rev.16-12/97
~
C PS-ODCM 6.3.3 Total Dose Section 4.1: Total Dose l) ,This requirement is provided to meet the dose limitations
'of 40CFR Part 190 that have been incorporated into 10CFR 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 effluents and direct radiation exceed 25 mrem to the total body or any organ, except the thyroid, which shall be limited to less than or equal to 75 mrem. For sites containing up to 4 reactors, it is highly unlikely that the resultant dose to a MEMBER OF THE PUBLIC will exceed the dose limits of 40CFR Part 190 if the individual reactors remain within twice the dose design objectives of Appendix I,. and if direct radiation doses from the
- ireactor units and outside storage tanks are kept small.
-Tlua Special Report will describe a course of action that
'should result in the Ibnitstion of the annual dose to a MEMBER OF THE PUBLIC to within the 40CFR Part 190 limits.
For the purposes of the Special Report, it may be assumed that the dose commitment to the MEMBER OF THE PUBLIC from other uranium fuel 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 NEMBER OF THE
- j. PUBLIC is estimated to exceed the requirements-of 40CFR
/' Part 190, the Special Report with a request for a variance (provided the release conditions resulting in violation of 40CFR Part 190 have not already been corrected), in accordance with the provisions of 40CFR Part 190.11 and 10CFR Part 20.2203, is considered to be a timely request and fulfills the requirements of 40CFR
' Part 190 until NRC staff action is completed. The variance only relates to the limits of 40CFR Part 190, and does not apply in any way to the other requirements for dose limitation of 10CFR Part 20, as addressed in Sections 2.3 and 3.4. An individual is not considered a
!i3MBER 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.
*h )
CLINTON-1 6-9 Rev.16-12/97
CPS-ODCM. , 46 . 4 Radiological Environmental Monitoring Section 5.1: Monitoring Program
,The radiological environmental monitoring program (-
' required by this require' ment provides representative measurements 'of radiation.and of radioactive materials in those exposure. pathways and for those radionuclides that lead to the highest potential radiation exposures of MEMBERS OF THE PUBLIC resulting from the station operation. This monitoring program implements Section IV.B.2 of Appendix I to '10CFR Part . 50 and thereby supplements the radiological effluent monitoring program by verifying that tne 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 fs provided by the Radiological. Assessment Branch Technical Position on Environmental Monitoring, Revibion 1, Novedoer 1979. The initially specified monitoring 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. I The required detection capabilities for environmental j
)' sample analyses are tabulated in terms of the lower limits of detection (LLDs). The LLDs required by Table S.1-3 are considered optimum for routine environmental
[ measurements in industrial laboratories. It should be recognized that the LLD is defined.as an a priori (before l the fact) ' limit representing the capability of a ) measurement system and not as an a posteriori (after the fact) limit for a particular measurement. Detailed discussion of the LLD, and other detection limits, can be found in Currie, L. A., " Lower Limit of
. Detection: Definition and Elaboration of a Proposed Position for Radiological Effluent and Environmental Measurements," NUREG/CR-4007 (September 1984), and in the HASL Procedures Manual, EASL-300 (revised annually).
Section 5.2: Land Use Census This requirement 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 l l
.~ 1
) l ( . CLINTON-1 6-10 Rev.16-12/97 4
CPS-ODCt4 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, questionnaire, or from consulting with local agricultural authorities).
) ,This census satisfies the requirements of Section IV.B.3
'of Appendix I to 10CFR Part 50. Restricting the census to gardens of greater than 50 m* provides assurance that significant exposure pathways via leafy vegetables will be identified and monitored since a garden of this size is the minimum required to produce the quantity (26 kg/ year) of leafy vegetables assumed in Regulatory Guide 1.109 for consumption by a child. To determine this minimum garden size, the following assumptions were ma'de:
(1) 20% of the garden was used for growing broad leaf l vegetation (i.e., similar to lettuce and cabbage) and (2) a vegetation yield of 2 kg/m*. Section 5.3.1: Interlaboratory Comparison Program ( The requirement for participation in an approved l 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 qual'ity 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 10CFR Part l 50.
-)
1 i i ( l l l I)' CLINTON-1 6-11 Rev.16-12/97
CPS-ODCM - 7.0 REPORTING REQUIREMENTS , 7.1 Annual Radiological Environmental Operating Report I -
." Routine Radiologica'l Environment'al Operating Reports
( covering tne operation of the unit during the previous calendar year shall be submitted prior to May 1 of each year pursuant to Technical Specification 5.6.2. The Annual Radiological Environmental Operating Reports shall include the following information: t 1. 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,
- 4 and with previous environmental surveillance.
l l ,- reports, and an assessment of the observed impacts of the plant operation on the environment. l l 2. The results of land use censuses required by Section-l 5.2. l
- 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 'acst two legible maps
- covering all sample locations keyed to a table giving distances and directions from the IWAC stack.
One map shall cover stations near the site boundary and a second map shall include the more distant stations.
)
l I CLINTON-1 7-1 Rev.16-12/97 l
CPS-ODCM
- 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 f schedule of Table 5.1-1. {
- 8. Discussion of all analysis in which the LLD required by Table 5.1-3 was not achievable.
7.2 Radioactive Effluent Release Report Routine Radioactive Effluent Release Reports covering the operation of the unit during the previous 12 months of operation shall be submitted by May 1 of each year pursuant to Technical Specification 5.6.3.
- The Radioactive Effluent 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 Radioac'tivity 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 10CFR Part 61), type of container (e.g., LSA, Type A, Type B, Large Quantity), and SOLIDIFICATION agent or absorbent (e.g., cement, urea formaldehyde). I 12 . The following information for each class of solid waste (as defined by 10CFR 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 whether determined by measurement or estimate),
))
{ CLINTON-1 7-2 Rev.16-12/97
C PS-ODCM ' l d. Source of waste and processing employed (e.g., , dewatered spent resin, compacted dry waste, evaporator bottoms).
' f_ .
,3. A list and description of unplanned releases from
( the site to UNRESTRICTED AREAS of radioactive materials in gaseous and liquid effluents made during the reporting period.
- 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 ODaH pursuant to Technical Specification 5.5.1.
- 6. Major changes to radioactive liquid, gaseous, and
- i solid waste treatment systems . The discussionsof
; each change shall contain:"
- a. A summary of the evaluation that led to the l
determination that the change could be made in. accordance with 10CFR Part 50.59.
- b. Sufficient detailed information to totally supporc 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; Licensees may choose to submit the information called for in this requirement as part of its annual USAR update.
Changes described by this requirement shall become effective upon review by the FRG.
~
I
. CLINTON-1 7-3 Rev.16-12/97
. C PS-ODCM
- 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 g) general population that differ from those
/- ,
- previously estimated in the. license application t- 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 a're 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.
'The ' Radioactive Effluent Release Report shall also include the following.information:
- 1. An. annual summary of hourly meteorological data collected over the previous year. This annual summary may be either in the form of an hour-by-hour listing on magnetic tape of wind speed, wind direction, atmospheric stability, and precipitation (if measured), or in the form of joint frequency-
);
distributions of wind speed, wind direction, and atmospheric stability.
- 2. An assessment of the radiation doses due to the radioactive liquid and gaseous effluents released from the unit or station during the previous I calendar year.
l
.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. Annual average meteorological conditions or meteorological conditions concurt.nt with the time of release of radioactive materials-in gaseous
~
effluents, as determined by sampling frequency and i measurements, may be used for determining the gaseous
\h l
CLINTON-1 7-4 Rev.16-12/97 l
)
CPS-ODCM
- 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 most. exposed MEMBER OF THE PUBLIC from reactor releases (. . l ' 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 40CFR Part 190, Environmental Radiation Protection Standards for Nuclear Power Operation. Acceptable methods for calculating the dose contribution i from liquid and gaseous effluents are given in Regulatory Guide 1.109, Rev. 1, October 1977. j 1 l
)1 3
1 l l
} l 1
l CLINTON-1 7-5 Rev.16-12/97
CPS-ODCM 8.0 ADJUSTMENT OF THE CPS ODCM METHODOLOGY Consistent with the NRC Commissioners' opinion on 10CFR50 Appendix I dated April 30, 1975, CPS will use pnvironmental 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 radioiodine-milk pathway where conservative regulatory guide assumptions have been made. By using environmental monitoring data, uncertainties associated I with plume behavior, radiciodine chemical form, deposition and retention of forages, and milk consumption patterns may be circumvented or reduced.
. a l
l) l
}
}l CLINTON-1 0-1 Rev.16-12/97
CPS-ODCM - 9.0 ATMOSPHERIC TRANSPORT AND DISPERSION MODEL . 9.1 Introduction i , 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 meteorological and dose calculations prescribed in this manual are based on meteorological data concurrent with the time of release or the annual average values. i Near-real time meteorological data processing is i
- '. prescribed in Section 9.2. l l
9.2 Concurrent Meteorological Data Processing Meteorological data is acquired and processed through a model which utilizes bi-level hourly meteorological tower data or single level joi,nt frequency data to perform the required analysis. Three distinct release modes are treated: elevated, ground and mixed. A set of five output arrays are generated for each dose
; receptor location as follows:
Relative undecayed, undepleted plume concentration (X/Q) Relative decayed and depleted radioiodine and particulate concentration (D2DPXQ) Relative decayed noble gas concentration (D1XQ) Relative particulate and radioiodine deposition (D/Q) l i Standard deviations of the undecayed, undepleted plume concentrations 1 ( .- CLINTON-1 9-1 Rev.16-12/97
[
. CPS-ODCM Since the Regulatory Guide 1.111 depletion and deposition curves are defined only within the range encompassing 100 to 200,000 meters, analysis results are not considered valid outside this range. The }iI i -
following sections describe the calculations performed I ! by the transport and dispersion model for a one hour time interval. 9.2.1 Determination of Pasquill Stability Class j The Pasquill Stability Class is determined by l categorizing the temperature gradient, AT, into one of l several ranges between -0.900 and 0.900 *C/ meter i j according to the following equation: i AT = (Tu - T t) / (Hu - Ho) , *C/ meter (1) i where
- l
~ l Tu = Meteorological (met) tower upper level temperature, *C Tt= Meteorological tower lower level temperature, *C Hu = Meteorological tower upper level instrumentation height l
= 60 meters
.)] He = Meteorological tower level instrumentation height
= 10 meters AT is then classified according to the following scheme:
Pasquill Stability Defining Condition A (Extremely Unstable) -0.900 < AT $ -0.019 B -0.019 < AT $ -0.017 C -0.017 < AT $ -0.015 D (Neutral) -0.015 < AT < -0.005 E -0.005 < AT < 0.015 F 0.015 < AT < 0.040 G (Extremely Stable) 0.040 < AT < 0.900 Invalid AT < -0.900 or AT > 0.900
'\ )
CLINTON-1 9-2 Rev.16-12/97 1
CPS-ODCM - 9.2.2 Calculation of Stack Height Wind Speed . The wind speed at the release point (HVAC Exhaust Stack g or Standby Gas Treatment System Exhaust Stack) height, -, 4 [ STACWS, is calculated using the expressions: STACWS = WSPu (STACKH/Hu) ", meter /sec (2) P= [ log (WSPt /WSPu) ) / [ log (Ht /Hu) ], dimensionless (3) whera
=
WSPu Upper met tower level wind speed, meter /sec WSP t = 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 Release Mode and the Entrainment Coefficient The mode of. release can be elevated, ground or mixed; the latter being a combination of the first two. The g mode of release, as well as an entrainment coefficient, TCORR, are determined from the stack height, STACH, [ building height, BLDGHT, stack exit velocity, EXITV, and wind speed at the stack height, STACWS. For effluents exhausted from release points that are higher than twice the height of adjacent solid structures, 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 points or vents at the level of, or above, adjacent solid structures, but lower than elevated release points,
)
CLINTON-1 9-3 Rev.16-12/97
CPS-0DCM (6) 2 (BLDGliT) > STACKil > BLDGitT the release is treated as elevated, ground or mixed according to the following relationships: j TCORR = 0.00 if EXITV >5(STACWS) (7) ELEVATED: TCORR = 1.0 if EXITV < STACWS (8) GROUND: (9) MIXED: TCORR = 0.30-0.06(EXITV/STACWS) if 5(STACWS) > EXITV > 1.5 (STACWS) (10) TCORR = 2.58-1.58(EXITV/STACWS) if 1.5(STACWS) > EXITV > (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 then evaluated separately and the concentration X/Q calculated according to the fraction of the time each release occurs.
9.2.4 Calculation of Vertical Standard Deviation The vertical plume spread (vertical standard deviation), r, is a function of the distance from the release point to the reception point for a given
}; Pasquill stability class. The numerical value of r, if obtained by a polynominal fitting equation which simulates Figure 1 of Regulatory Guide 1.111:
+C (log (X) ) 2 } , meter (11) r, = 10 [ A + B log (X) where X = Distance to a specific receptor, kilometer A,B,C = Empirical factors which vary by stability class, determined by fitting polynominal equations to the Regulatory Guide 1.111 Figure 1 curves, dimensionless
)
9-4 Rev.16-12/97 CLINTON-1
CPS-ODCM Empirical Factors Used in Equation (11) - Pasquill Class A B C l A 2.79166 2.69043 1.07483 I 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 be specified which limits the value of r, to be no greater than this value. 9.2.5 Calculation of the Building Wake Correction For ground-based and mixed-mode releases, an adjustment is made in the calculation of X/O that takes inta 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): I,= [a,* + 0.5 (BLDGHT)*/x]h (12) I with the requirement that E* is restricted to values { E 5 (3)N (c2) . 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 of the exhausted effluent, AH, is calculated. For Pasquill stability classes A,B,C and D, AH is calculated per section 9.2.6.1; for classes E,F and G, section 9.2.6.2 is used. 9.2.6.1 AH For Pasquill Class A,B,C and D AH is calculated using both equations (13) and (14) and the minimum value is selected for use. In addition, when the vertical exit velocity,-EXITV, is less than 1.5 times the horizontal windspeed, STACWS, a downwash correction is subtracted from equation (13) per equation (15).
)
CLINTON-1 9-5 Rev.16-12/97
CPS-ODCM AH 3 = 1. 4 4 (STACD) (EXITV/STACWS) (13) (X/STACD)"#-DOWNWASH, meter
') (14)
[ AH 2 = 3. 0 (STACD) (EXITV/STACWS) , meter DOWNWASH = 3. 0 (STACD) (1. 5-EXITV/STACWS) , meter (15) l where STACD = Internal release point stack diameter
= 3.77 meters (HVAC Exhaust Stack)
= 0.44 meters (SGTS Exhaust Stack)
EXITV = Stack exit velocity, meter /second X = Distance to specified receptor, meter
- + All other parameters are as defined previously.
9.2.6.2 AH For Pasquill Class E,F and G AH is determined by selecting the minimum value calculated by equations (13) and (14) above and equations (16) and (17) below: AH 3 = 4. 0 [ (0. 5 (EXITV) (STACD) ) */S] , meter (16)
)) AH 4 = 1. 5 [ ( 0. 5 (EXITV) (STACD) ) #/ STACWS ] * (S) '*",
meter (17) where S= Restoring acceleration per unit vertical ~ displacement for adiabatic motion, sec#
= 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 Height 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)
}}
CLINTON-1 9-6 Rev.16-12/97
C PS-ODCM - where - TERAIN = Difference between the plant base height
-) above mean sea level (MSL) and the receptor
{~ x
. point height above HSL, meter >0.0.
9.2.8 Determination of Affected Sectors 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) J Number Direction 1 N 0.0* < WD < 11.25" or 348.75* 2 WD < 360.00*
- "' 2 NNE 11.25* 2 WD 2 33.75*
3 NE 33.75* 2 WD < 56.25* 4 ENE 56.25* 2 WD < 78.75* 5 E 78.75* 2 WD < 101.25' 6 ESE 101.25* 2 WD < 123.75* 7 SE '123.75* 2 WD < 146.25' 8 SSE 146.25* 2 WD < 168.75* 9 S 168.75* 2 WD < 191.25* 10 SSW 191.25* 2 WD < 213.75* 11 SW 213.75* 2 WD < 236.25*
- 12 WSW 236.25* 2 WD < 258.75*
13 W 258.75* 2 WD < 281.25* (. 14 WNW 281.25* 2 WD < 303.75* 15 NW 303.75* 2 WD < 326.25* 16 NNW 326.25' 3 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 same at both levels, the resulting X/O will be summed into the same sector; 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. ) ( _ CLINTON-1 9-7 Rev.16-12/97
CPS-ODCM 9.2.9 Calculation of Depletion 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 polynominal equations developed to simulate the Regulatory Guide curves. Both the DPF and DPSP calculations depend on the effective plume height, H, the stability class, S, and the distance, X, to the receptor. 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 meters above the
- 6 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 topography does change with 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 curve 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 Height (meters) J Value O < H < 15 5
~
6 15 < H $ 4 5 7 45 < H $ 80 8 H > 80 Similarly, the stability class is categorized into one of three S-ranges as follows: ,)> CLINTON-1 9-8 Rev.16-12/97
CPS-ODCM - Stability Class S. Value . A, B, C 1
') D 2
[ E, F, G 3 i 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 (meters) A DPF 5 X < 100 1.0 X > 100 A= 1 calculated 6 X 2 200 1.0 X > 200 A=5 calculated 7 X < 300 1.0 X > 300 A = 17 calculated
; 8 X 2 600 1.0 X > 600 A = 29 calculated 10 all X 1.0 12 X < 400 1.0 X > 400 A=9 calculated l 14 X 2 1000 1.0 l X > 1000 A = 21 calculated l
15 all X 1.0 16 X < 1700 1.0
) X > 1700 A = 33 calculated 18 X 2 6000 1.0 [
X > 6000 A = 13 calculated 21 X 2 60,000 1.0 X > 60,000 A = 25 calculated 24 all X 1.0 l DPF is calculated using th,e value for A and equations (19) and (20): DPF = B(A) + B (A + 1) d + B ( A + 2) d* + B ( A + 3) d' (19) d = log (X) (20)
)
CLINTON-1 9-9 Rev.16-12/97
CPS-ODCM The corresponding values for the B(A), B(A + 1), B(A +
- 2) and B(A + 3) terms are as follows:
's B(1) = .780234 B (19) = .426473
, B(2) = .207198 B(20) = -0.0471767 B(3) = .0563034 B (21) = .615442 B(4) = .0 B(22) = .317258 B(5) = 2.59500 B(23) = .0631839 B (6) = -1.43610 B(24) = .0 B(7) = .433300 B(25) = -6.89581 B(0) = .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 (meters) C DPSF 5 X < 100 0 X > 100 C=1 calculated 6 X 2 100 0 X > 100 C=8 calculated 7 X 2 100 0 X > 100 C = 29 calculated 8 X 2 100 0 X > 100 C = 50 calculated 10 all X 0 12 X < 100 0 X > 100 C = 15 calculated 14 X 2 120 0 X > 120 C = 36 calculated 15 all X 0 16 X < 210 0 X > 210 C = 57 calculated 18 X 2 2900 0 X > 2900 C = 22 calculated CLINTON-1 9-10 Rev.16-12/97
CPS-ODCM ' 21 X < 26,000 0
) X ,> 26,000 C = 43 calculated 24 all X 0 -
~
DPSP is calculated using the value for C and equations (20), (21), and (22): Y DPSP = 10 / (O.392699X) (21) l Y = A(C) + A (C+1) d + A(C+2) d* + A (C+3) d' (22)
+ A (C+4 ) d' + A) (C+5) d' + 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+5) and A(C+6) terms are as follows: A(1) = -3.17821 A(33) = 7.552876
- A(2) = .153463 A(34) =
.82569984 l A(3) = .0759066 A(35) =
.036134823 A(4) = 0. A(36) =
-53.7335 A(5) = 0. A(37) =
45.3671 A(6) = 0. A(38) = -15.3282 A(7) = 0. A(39) = 2.24735 A(8) = -25.7331 A(40) = .122674 A(9) = 26.2738 A(41) = 0. A(10) = -11.3014 A(42) = 0. f A(11) = 2.04278 A(43) = -674.351 fs A(12) = .134412 A(44) = 384.531 ( A (13) = 0. A(45) = -73.7766 A(14) = 0. A(46) = 4.72041 A(15) = -47.5827 A(47) = 0. A(16) = 43.8050 A(48) = 0. A(17) = -16.0781 A(49) = . O. A(18) = 2.53726 A(50) = -55.5622 A(19) = .148044 A(51) = 53.6534 A(20) = 0. A(52) = -20.6300 A(21) = 0. A(53) = 3.44177 A(22) = -128.5278 ~ A(54) = .212314 A(23) = 77.28943 A(55) = 0. A(24) = -15.90284 A(56) = 0. A(25) = 1.071885 A(57) = 436.987302 A(26) = 0. A(58) = -755.860224 A(27) = 0. A(59) = 515.64145 A(28) = 0. A(60) = -181.713295 A(29) = 41.824767 A(61) = 35.153579 A(30) = -103.969677 A(62) = -3.558356 A (31) = 86.215344 A(63) = .14774 A(32) = -35.1021096
]
CLINTON-1 9-11 Rev.16-12/97
C PS-O DCM 9.2.10 Ground Level X/O, D2DPXQ, D1XQ, D/O Analysis
, 9.2.10.1 Undecayed, Undepleted Plume Relative Concentration, X/Q
.' The atmospheric concentration of effluent at ground level, normalized by the source term,0, is given by the following equation:
X/O = 2.032 (TCORR) /WSPo(X) Amn, sec/m' (23) where Awn = The lesser of the two values obtained by equations (24) and (2 5) , meter A3 = (c', + I ) , meter (24) A2 = (3) o,, Meter (25) H 2.032 = The constant (2/x) divided by the width in radians of a 22.5" sector (i.e., x/8, dimensionless X = Distance between release point to receptor, meter
.} 9.2.10.2 Decayed, Depleted Radiciodine and Particulate Relative Concentration,.D2DPXO The decayed, depleted radiciodine concentration, D2DPXQ, is calculated in accordance with the following equation:
D2DPXQ = DPF(DC2)X/Q, sec/m' (26) where DPF = The depletion factor calculated per sectice 9.2.9, dimensionless DC2 = The radioiodine decay factor, dimensionless
= exp[-0.693 (X) /th(WSPt) ] ,
J
= exp[-0.693 (X) / (8 day) (24 hr/ day) (3'600 sec/hr) (WSPo) ] .
T i CLINTON-1 9-12 Rev.16-12/97
t' CPS-ODCM
= exp[-1.00E-06 (X/WSPt) ] .
9.2.10.3 Decayed Noble Gas Plume Relative Concentration, _D1XQ = t The decayed noble gas plume relative concentration, D1XQ, is calculated in accordance with the following equation: D1XQ = DC1 (X/0), sec/m' (27) where DC1 = The noble gas decay factor, dimensionless
= exp [-0. 693 (X) /ty(WSP )t )
= exp [-0. 693 (X) / (2.26 day) (24 hr/ day) __
(3600 sec/hr) (WSPt ))
= exp [-3.55E-06 (X/WSPo) )
9.2.10.4 Radioiodine and Particulate Relative Deposition, D/O The relative deposition for radiciodines and particulates, D/O is calculated in accordance with the following equation: D/O = [DPSF (DC2) (TCORR) ] / [ (2x/16) X) , ng2 (28) where DPSF = The deposition factor calculated per section
- 9. 2. 9, ni l 9.2.11 Elevated X/0, D2DPXQ, D1XQ, D/O Analysis 9.2.11.1 Undecayed, Undepleted Plume Relative Concentration, X/O The atmospheric concentration of effluent at elevated level, normalized by the source term O, is given by the following equation:
X/O = [2.033 (1-TCORR) exp[-0.5 (H/oz) 2 ] ] / [STACWS (X) oz), sec/m (29) where all parameters are as previously defined. CLINTON-1 9-13 Rev.16-12/97
I ' - C PS-ODCM 9.2.11.2 Decayed, Depleted 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 WSPo value used in the calculation of DC2.in equation (26) is replaced by the STACWS value and the equation (29) X/O is used. 9.2.11.3 Decayed Noble Gas Plume Relative Concentration,.D1XQ The calculation of D1XQ for elevated releases follows section 9.2.10.3 methodology by substituting the equation (29) X/Q value into equation (27) and STACWS for WSPo in the calculation of DC1. 9.2.11.4 Radiciodine and Particulate Relative Deposition, D/O
. a 7
The calculation of D/0 for elevated releases follows section 9.2.10.4 methodology by substituting (1-TCORR) for the TCORR term in equation (28) and STACWS for WSPt in the calculation of DC2.
.)
h I i
'g } .
1 CLINTON-1 9-14 Rev.16-12/97
CPS-ODCM Table 9.2-1 GASEOUS EFFLUENT RELEASE POINT CIIARACTERISTICS
= = aUu== --m mo /
ROOF El. 876'0* MAOCHE DIOP DUuma ROOF O. 781t* m 'M g_ > toe *o* _ CONTROL ROOW - r SCTS YD(T AIRIWOUNG
\ UNITS TOP CONTAlguD(T CONC.EL 927'0* C 6 -
A courRa.sa m ROOP EL 847%* 1 l>
/. nn 69 (di p
N I ( BUU)tNG
/ ROOF EL 790'0* (FLP.)
i /. vvanuuma ROOF EL 800'0*
/
3.
\/
/
/
/
ROOLEL 788'0' (LP.) 4 p __ __==Ef.5~ .b. .,q ,,
, m aca.uo me.uu=G g ~ mirutRum (a a.710 0-)
~~~ G -. ___ 'l l
HVAC Exhaust SGTS Exhaust Stack Stack-Release Point Height (m) 61 61 Building Height (m) 58 58 Release Point Geometry Duct Pipe 2 Release Point Area (m ) 11.15 0.15 Release Point Diameter (m) 3.77* 0.44 Annual Average Flow Rate (m'/ s ec) 111.71 1.89
) Vertical Ex.it Velocity (m/sec) 10.02 12.49 1
*Ef fective 2 (A/n) diameter CLINTON- 1 9-15 Rev.16-12/97}}