ML20059E650
| ML20059E650 | |
| Person / Time | |
|---|---|
| Site: | Limerick  |
| Issue date: | 04/03/1990 |
| From: | Mccormick M PECO ENERGY CO., (FORMERLY PHILADELPHIA ELECTRIC |
| To: | |
| Shared Package | |
| ML20059E608 | List: |
| References | |
| PROC-900403, NUDOCS 9009100265 | |
| Download: ML20059E650 (218) | |
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PHILADELPHIA ELECTRIC COMPANY t LIMERICK GENERATING STATION ! UNITS NO. 1 AND 2 DOCKET No. 50-352 (Unit 1) , DOCKET NO. 50-353 (Unit 2) l l l n t SEMI-ANNUAL EPPLUENT RELEASE. REPORT ' NO. 12 JANUARY 1, 1990 THROUGH JUNE 30, 1990 Attachment ' D.. Offsite Dose Calculations Manual, Revision'8 [ l l l 1 l ,
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3904052100 OFFSITE DOSE CALCULATION MANUAL
- i REVISION 8' '
f i i i LIMERICK GENERATING STATION ,
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i l UNITS 1 AND 2 ' f PHILADELPHIA ELECTRIC COMPANY . DOCKET NOS. 50-352 and 50-353 i
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PORC Approval: , h / /10 Q Manster ! j Radiation Control and Chemistry t Nuclear and Environmental / Soction Approval: h* . '
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l LGS Health Physics Representative 6 C' 4 F / d b d W H / l 1 Radiation Control and Chemistry /
- E Nuclear and Environmental . > -
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l ODCM 8 Offsite Dose Calculation Manual 04/03/90 08/13/86 l i 4 e I l e a b9 4
stodem i Table of contents Page +. Introduction 1 Part I - Radiological Effluent Controls
- 1. 0' Definitions - I,-1 2.0 Basis for Effluent Monitoring Controls I-7 '
2.1 Meteorological Monitoring Instrumentation I-7 2.2 Maps defining unrestricted areas and site boundary for 1 radioactive gaseous and liquid effluents I-7 : 2.,3 Radioactive Liquid Effluent Monitoring Instrumentation I"7 2.3.1 Concentration I-12 2.3.2 Dose I-12 2.3.3 Liquid Radwaste Treatment System I-13 l 2.4 Radioactive Gaseous Effluent Monitoring Instrumentation I-13 : 2.4.1 Dose Rate I-13 2.4.2 Dose - Noble Gases I-14 2.4.3 Dose - Iodine-131, Iodine-133, Tritium, and Radionuclides in Particulate Form I-14 Ventilation Exhaust Treatment System 2.4.4 I-15 2.4.5 Venting and Purging . I-16 2.4.6 Total-Dose I-16 2.5 Monitoring Program I-17 ; 2.5.1 Land Use Census I-17 2.5.2 In'terlabora' tory Comparison Program I-17 ' 2.6 Applicability I-18 3.0 Effluent Controls I-20 3.1 Meteorological Monitoring Instrumentation I-20 1 49
l 0 3.2 Liquid Effluents I-25 3.2.1 Radioactive Liquid Effluent Monitoring-Instrumentation , I-25 3.2.2 Concentration I-28 3.2.3 Dose I-32 3.2.4 Liquid Radwaste Treatment System I-33 3.3 Gaseous Effluents 3.3.1 Radioactive Gaseous Effluent Monitoring Instrumentation I-34 3.3.2 Dose Rate I-41 3.3.3 Dose - Noble Gases I-45 3.3.4 Dose - Iodine-131, Iodine-133, Tritium, and Radionuclides in Particulate Form I-46 3.3.5 Ventilation Exhaust Treatment System I-47 3.3.6 Venting or Purging I-48 3.3.7 Total Dose .I-49 3.4 Radiological Environmental Monitoring i 3.4.1 Monitoring Program -50 i 3.4.2 Land Use Census I-62 1 3.4.3 Interlaboratory Comparison Program I-63 3.5 Annual Radiological Environmental Operating Report I-64 3.6 Semiannual Radioactive Effluent Release Report I-65 3.7 Major Changes to Radioactive Waste Treatment Systems I-67 11 ,
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- a LIMERICK GENERATING STATION OPFSITE DOSE CALCULATION MANUAL TABLE OF CONTF.NTS -
3 II.' Calculational Methodologies ' 1.0 Liquid Effluents 1.1' Radiation Monitoring Instrumentation and Controls .
, 1 1.2 Liquid Effluent Monitor Setpoint Determination 1 1.2.1 Radwaste Discharge Monitor {
2 j 1.2.2 Service Water Radiation Monitor 6 1.2.3 RHR Service Water Monitor 7 1.'3 Liquid Effluent Dose Calculations - 10 CFR 50 8 i. 1.3.1 Member of the Public Dose - Liquid Effluents 8 1.4 Liquid Effluent Dose Projection 14 l 2.0 Gaseous Effluents 2.1 Radiation Monitoring Instrumentation and Controls 15 2.2 Caseous Effluent Monitor Setpoint Determination 16 2.2.1 North Vent Noble Gas Effluent Monitors . 19 2.2.2 , South Vent Noble Gas Effluent Monitors 22 l 2.2.3 Noble Gas Effluent Fractional Contribution 25 2.2.4 Noble Gas Effluent Default Setpoints 27 2.2.5 < WRAM Noble Gas Effluent Monitor 31 2.3 Gaseous Effluent Dose Evaluations 38 2.3.1 Site Boundary Dose Rate - Noble Gases
. 39 2.3.2 Site Bounda'ry Dose Rate - Radiciodine and '
Particulates 43 i 2.3.3 Noble Gas Air Dose ' 44 2.3.4 Radiolodine 10 CFR 50 and Particulate Dose Calculations ' 46 i ll - b9 t
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4 2.3.5 Annual Dose Evaluation 50 2.4 Gaseous Effluent Dose Projection 55 3.0 Special Dose Analysis 56 3.1 Total Doses to Members of the Public 56 3.2 DosesDuetohetivitiesInsidetheSiteBoundary 57 4.0 Radiological Environmental Monitoring Program 59 4.1 Sampling Program 59 4.2 Interlaboratory Comparison Program 60
, APPENDICES l
Appendix A - Technical Specification /ODCM Matrix j Appendix B - Radiological Environmental Monitoring Program - Sample Type, Location and Analysis
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4 LIST OF TABLES r I 3.1-1 Meteorological Monitoring Instrumentation ,
- I 3.1-2 Meteorological Monitoring Instrumentation Surveillance Requirements !
I 3.2-1 Radioactive Liquid Effluent Monitoring Instrumentation I 3'.2-2 Radioactive Liquid Effluent Monitoring Instrumentation , Surveillance Requirements i. I 3.2-3 Radioactive Liquid Waste Sampling and Analysis. Program' ! I 3.3-1 Radioactive Gaseous Effluent Monitoring Instrumentation t I 3.3-2 Radioactive Gaseous Effluent Monitoring Instrumentation Surveillance Requirements I'3.3-3 Radioactive Gaseous Waste Sampling and Analysis Program I 3.4-1 Radiological Environmental Monitoring Program ' I 3.(-2 Reporting Levels for Radioactivity Concentrations In Environmental Samples I 3.4-3 Detection Capabilities For Environmental Sample Analysis l ! II l-1 l Ingestion Individual Dose Factors (Daipj) For Liquid Effluents ' II 1-2 Assumptions Used In Limerick Liquid Effluent Dose Evaluations . II 2-1 Dose Factors For Noble Cases + II 2-2 Individual Dose Factors (DFk,1,n) For Gaseous Effluents II 2-3 Assumptions Used In Limerick Gaseous Effluent Dose Evaluation , II 2-4 Nearest Gaseous Effluent Dose Receptor Distance,s (Meters) A-1 Technical Specification /ODCM Matrix B-1 Radiological Environmental Monitoring Program l l 1 j V mo I i
LIST OF FIGURES I 2.1-1 Meteorological Tower Location I 2.2-1 Map Defining Unrestricted Areas for Radioactive Gaseous and Liquid Effluents I 2.2-2 Map Defining Unrestricted Areas for Radioactive Gaseous and Liquid Effluents . , II 1.3.1-1 LGS Dilution vs River Flow (Outfall) II 1.3.1-2 LGS Dilution vs River Flow (Citizen's Utility) II 1.3.1-3 LGS Dilution vs River Flow (Phoenixville) II 1.3.1-4 LGS Dilution vs River Flow (Philadelphia Suburban) II'1.3.1-5 LGS Dilution vs River Flow (Crew Course) II l-1 Liquid Effluent Flow Diagram II 2-1 Gaseous Effluent Flow Diagram - North Stack II 2-2 Gaseous Effluent Flow Diagram - South Stack II 2-3 Gaseous Effluent Flow Diagram - Hot Maintenance Shop B-1 Environmental Sampling Locations on Site or Near i the Limerick Generating Station B-2 Aquatic and Terrestrial Environmental Sampling Locations at Intermediate Distances from the Limerick Generating Station B-3 Airborne and TLD Environmental Sampling Locations at Intermediate Generating Distances'from the Limerick Station B-4 Environmental Sampling Locations at Remote Distances from the Limerick Generating Station O $
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. . 1 TABLE A-1 i
TECHNICAL SPECIPICATION/ODCM MATRIX ! ODCM ODCM I Technical Section I Equation Specification Recuirement 8ection II 6.8,.4.d.1 3.2.1 1-1 - 1-2* . , 1-3 ! 1-4 1 1 6.8.4.d.1 3.3.1 2-1 (or 2-9) l 2-2 (or 2-9) l 2-4 (or 2-10) i 2-5 (or 2-10) ' 6.,8.4.d.2,d.3 3.2.2 1-1 1 1-2 1-3 1-4 6.8.4.d.4 3.2.3 1-5 1-6 1-7 6.8.4.d.5,d.6 3.2.4 1-8 1-9 6.8.4.d.7 ,3.3.2 2-22 ' 2-23 6.8.4.d.7 3.3.2 2-26 2-27 2-28 6.8.4.d.8 3.3.3 , 2-24 2-25 -t 6.8.4.d.9 3.3.4 2-26 2-27 2-28 6.8.4.d.9 ,
,3.3.5 2-33 3.11.2.7 2-4 3
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i TABLE A-1 (cont.) i ODCM ODCM Technical Section I Equation Specification Requirement j Section7II -! 6.8.4.d.10 3.3.8 1-5 1 I 1-6 1-7 2-24 i 2-25 . , l 2-26 ' 2-27 2-28 6.8.4.d.10 3. 3. 7 ' 3-1 i 6.8.4.e.1 3.4.1 Section 4 App. B 6.'8.4.e.3 3.5 1-5 3.4.3 1-6 1-7 2-29 2-30 2-31 2-32 3-2 4 i k i e
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L . . DEFINITIONS I The.following-terms are defined so that uniform interpretation of l these controls may be achieved. The-defined terms appear in: { capitalized type and shall'be applicable.throughout these l controls. - I l 1.1 ACTION- . ACTION shall be that'part of a control which prescribes. 3
' remedial measures: required under designated conditions.
- 1. 2 - CHANNEL CALIBRATION 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 1 parameter which the channel. monitors. The CHANNEL- _ f
' CALIBRATION.shall encompass the entire channel including i the sensor andJalarm and/or trip functions, and shall ,
, include the CHANNEL FUNCTIONAL TEST. The-CHANNEL !
g CALIBRATION may be performed by any series of sequential, overlapping or total 1 channel steps such that the entire ' channel is calibrated. 1.3 CHANNEL CHECK A CHANNEL CHECK shall be the qualitative assessment of-channel behavior during operation by observation. This l. 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. 1.4
]l CHANNEL FUNCTIONAL TEST A CHANNEL FUNCTIONAL TEST shall bet
- a. Analog channels - the injection of a simulated signal into the channel as close to the sensor as practicable to verify OPERABILITY including alarm and/or trip functions and channel failure trips,
- b. Bistable channels - the injection of a simulated signal into the. sensor to verify OPERABILITY including alarm L
and/or trip functions. < TheCHANNEL-FUNCTIdNALTESTmay,be.performedbyanyseries of sequential, overlapping or total channel steps such that i the entire channel is tested. - Engr. 7/4/ ' B .' P . exa I-l Date ::NPo 1 l Rev. 9? w,- 1
- - _ +
105 DOSE EQUIVALENT I-131 DOSE EQUIVALENT I-131 shall be that concentration of I-131, microcuries per gram, which alone would produce the same thyroid dose as the quantity and isotopic mixture of I-131, ' I-132, 1-133, I-134, and I-135 actually present. The thyroid dose conversion factors used for this asiculation shall be those listed in Table III of TID-14844,
" Calculation of Distance Factors for Power and Test Reactor Sites."
- 1. 6' FREQUENCY NOTATION -
The FREQUENCY NOTATION specified for the performance of Surveillance Requirements shall correspond to the intervals defined in Table I.1. 1.7 MEMBER (S) OF THE PUBLIC MEMBER (S) OF THE PUBLIC shall include all persons who are not occupationally associated with the plant. This estegory does not include employees of the utility, its contractors, or vendors. Also excluded from this category are persons who enter the site to service equipment or to make deliveries. This category does include persons who use portions of the site for recreational, occupational, or other purposes not associated with the plant. 1.8 OFFSITE LOSE CALCULATION MANUAL The OFFSITE DOSE CALCULATION MANUAL (ODCM) shall contain the methodology and parameters used in the calculation of offsite doses resulting from radioactive gaseous and liquid effluents, in the calculation of gaseous and liquid effluent monitoring Alarm / Trip Setpoints, and in the conduct Program. of the Environmental Radiological Monitoring The ODCM shall also contain (1) the Radioactive Effluents Controls and Radiological Environmental Monitoring Programs required by Technical ?S ecification 6.8.4 and (2) descriptions of the information that should be included in the Annual Radiological Env.ronmental Operating and Semi-annual Radioactive Effluent Release Reports required by Technical Specifications 6.9.1. 7 and 6.9.1.8. (3) description of meteorological monitoring controls. Engr. H. P. Date S ts Rev. F I-2 b4
- 1, 9_ ' . OPERABLE -OPERABILITY-A system, subsystem, train, component or device shall- be -
- OPERABLE or have OPERABILITY when it is capable of :
performing >its specified function (s) and when all necessaryf attendant instrumentation, controisi electrical power,
cooling or' seal water', lubrication or other auxiliary
_ equipment;that are' required for the system, subsystem,1 train, component, or device to perform its function (s) are .; also: capable of performing their related support
, function (s). ;
1.10 OPERATIONAL CONDITION - CONDITION' An OPERATIONAL' CONDITION, i.e., CONDITION, shall be.any'one j
' inclusive combination of' mode switch position:and average {
reactor. coolant temperature as defined lin the Technical j Specifications.
'l.11 PURGE -' PURGING
~ PURGE or PURGING shall be the" controlled processLof-discharging air or, gas from a-confinement to-maintain- s temperature, pressure,-humidity, concentration or other operating condition, in'such a manner that replacement air. [
or - gas is required- to purify the confinement. : ? 1.12 RATED THERMAL POWER RATED THERMAL POWER shall be a total reactor core heat l transfer rate to the reactor coolant of 3293 MWt. 1.13 REPORTABLE EVEET < i A REPORTABLE EVENT shall be any of those conditions specifiedLin Section 50.73 to 10 CFR Part 50. 1.14 SITE BOUNDARY j The SITE BOUNDARY shall be'that line gs defined.'in Figure 12.2-la. 1.15 SOURCE CHECK- ! A SOURCE CHECK shall be'the qualitadive assessment.of-channel response when the channel ~ sensor is; exposed to a '
. radioactive source.,_
l.16 THERMAL POWER THERMAL POWER shall be the total reactor core heat transfer i rate:to the reactor coolant. I-3 . Date 3 fo ' bT
. . .,.."ri 4
l'17
. I UNRESTRICTED AREA '
An UNRESTRICTED' AREA shall be any area at or beyond the SITE BOUNDARY access to'which-is not. controlled by the-licensee for purposes of protection of-individuals exposure-to radiation and radioactive materials, or;from any '- area within.the SITE BOUNDARY used forl residential quarters or for industrial, recreational commercial, institutional, and/or purposes.
- l.1{ VENTILATION EXRAUST TREATMENT SYSTEM.
A VENTILATION EXHAUST TREATMENT SYSTEM shall be any system designed and installed to reduce gaseous.radioiodine or radioactive passing material'in ventilation or v; particulate form.in effluents by ent exhaust gases through. charcoal adsorbers. and/or HEPA filters for the purpose; of: removing
-iodines' or particulates_ f rom the gaseous exhaust stream prior to the release to'the environment-(such a system is not considered to-have anyfeffect on noble gas. effluents).
Engineered = Safety Feature-(ESP)' atmospheric cleanup systems 1 are not considered to be VENTILATION EXEAUST TREATMENT SYSTEM-components.- l
'l.19 --VENTING VENTING shall be>the controlled processiof discharging air or gas from a confinement to maintain temperature,
. pressure, humidity, concentra' condition, in such a manner s
'r other operating not provided or required dur valacement air or gas is
,tNG. Vent, used in system names, does not. imply a J ._NG process.
i a Engr.'Qldh H. P. '%22f . R ? ~% I-4 - we l a .. _
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- TABLE'1.1 SURVEILLANCE'rREQUENCY NOTATION NOTATION FREQUENCY S At least once per 12 hours.
D At least once per:24 hours.
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W At leact' once_per 7 days. M' _At least'o.'ce per_31 days. l Q x At 16ost once_per192-days. SA At least once per 184 days. i
,A At least;once_per 366 days. -!
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At least once-per 10, months (550. days), i S/U Prior to each reactor:startup.
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P Prior to~each radioactive ~ release.'- . ; N.A. . Not applicable. i I i l I. 4 4 4 Engr. H. P.. ACR; , ev I-5 ! I
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' slPg8 3/4 3-4odem:74 - RWG 2.0 BASES FOR EFFLUENT MONITORING CONTROLS. ,
2.1 METEOROLOGICAL MONITORING INSTRUMENTATION The OPERABILITY of the meteorological monitoring ' instrumentation ensures that sufficient meteorological data is - available for estimating potential radiation doses to the public as a result of routine or accidental release of radioactive materials to the atmosphere. This capability is required to evaluate the need for initiating protective measures to protect the health and safety of the public. This instrumentation is conhistent with the recommendations of Regulatory Guide 1.23 -
"Onsite Meteorological Programs," February, 1972.
Site data compiled since January 1972 provide correlation l between Elevation 1 (lower 1) and Elevation 1 (Tower 2 , and betweenElevation2(Tower 1)andElevation2(Tower correlation serves as justification for the use of the
) 2).-Thit !
appropriate Tower 2 instrument as a back-up to the Tower 1 instrument as shown in Table 1 3.1-1. ' KAPS DEFINING UNRESTRICTED AREAS AND SITE BOUNDARY FOR RADIOACTIVE GASEOUS AND LIQUID EFFLUENTS < 2.2 -Information regarding radioactive gaseous and liquid effluents, which will allow identification of structures and release points as well as definition of UNRESTRICTED AREAS within the SITE BOUNDARY that are accessible to MEMBER OF THE PUBLIC, shall be shown in Figures 12.2.-ia and 12.2.-lb. The exclusion area and low population zone shall be as shown in Figures 12.2.-1c.and 12.2-1d. 2.3 RADIOACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION The radioactive liquid effluent instrumentation is provided to monitor and control, as applicable, the releases of ' radioactivematerialsinliquideffluentsduringactualor potential releases of_ liquid effluents. The alarm / trip setpoints for these instruments shall be calculated in accordance with the procedures in the ODCM part 11 to ensure that the alare/ trip will occur prior to exceeding the limits of 10 CFR Part 20. The OPERABILITY and use of this instrumentation is consistent with the requirements of General Design Criteria 60, 63, and 64 of Appendix A to 10 CFR Part 50. , Engr.Gh H. P. ' Date ' Rev. , l I-7
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Date 90 Rev. 1-11 b% ____.__._________.______.____-_____. __.,,._,..._.4_.._.,._.,;.. _ ....__,....,r,,- ,,, , .. - . ., . . _ . - - - , . _ - . . . - . , ,
' s;PgB3/4 ll-lodcJn: 74[RWG 2.3.1 CONCENTRATION This control is provided to ensure that the concentration of radioactive materials released in liquid waste effluents to UNRESTRICTED AREAS vill be less ;
.than Columnthe2. concentration levels specified in 10 CFR Part 20, Appendix B, Table II, This limitation provides additional assurance that the levels of i radioactive materials in bodies of water in UNRESTRICTED AREAS will exposures within (1) the Section ll.A design objectives of Appendix 1,10 CFR '
Partpopulation. the 50, to a MEMBER OF THE PUBLIC, and (2) the limits of 10 CFR 20.1')6(e) to The concentration limits for dissolved or entrained noble gases are based upon the assumption that Xe-135 is the controlling radioisotope and its MPC in air was converted to an equivalent concentration in water using the , methods described (ICRP) Publication 2. in the International Commission on Radiological. Protection 4 The required detection capabilities for radioactive materials in liauid 3 waste samples are tabulated in terms of the lower limits of detection (LLDs). Detailed discussion of the LLO, and other detection limits can be foul.d in HASL Procedures Manual,_HASL-300 (revised annually), Currie, L. A., " Limits for Qualitative Detection and Quantitative Determination - Application F.adiochemistry," Anal. Chem. 40. 586-93 (1968), to J. K., " Detection Limits for Radioanalytical Counting Techniques." Atlantic Richfield Hanfand Hartwell ord Comoany Report ARH-SA-215 (June, 1975). ~ _2.3.2 DOSE I!!.A, and IV.A of Appendix I, 10 CFR Part 50.This Control is provided to i . guides set forth in Section II.A of Appendix 1. The Control implements the The ACTION statements provide forth in Section IV.A of Appendix ! to assure that the release material in liquid effluents will be kept "as low as is reasonably-achievable " ; Also, for fresh water sites with drinking water supplies which can be . operation of the facility will not result in radionuclide concen - 141. finished drinking water that are in excess of the requirem , requirements in Section Ill.A of Appendix 1 that conformance with the guides of Appendix ! be shown by calculational procedures based on models , such and data that the actual is unlikely exposure underestimated. to be substantially of a MEMBER OF THE PUBLIC through appropriate pa ODCH for calculating the doses due to the actual release rates of radioactiveThe materials in liquid effluents are consistent with the methodology provided in Regulatory Guide 1.109, " Calculation of Annual Doses to Man from Routine Releases CFR Part 50,of Reactor Appendix Effluents for the Purpose of Evaluating Compliance with 10 I," Revision 1, October,1977 and Regulatory Guide'1.113 .
" Estimating Aquatic Dispersion'of Effluents from Accidental and Routine Reactor Releases for the Purpcse of implementing Appendix I," April,1977.
effluents from the site.This control applies to the release of radioactive materials in liqu 4 Engr. ' 1-12 H. P. Date 70 Rev. -
., \
~ ~ _ . _ _ _ _ _ _ _ _ _ _ _ _ _ _ . _ _ _ __
2.3.3 L10VID RADWASTE TREATMENT SYSTEM _ The requirement that the appropriate portions of this system be.used when specified provides kept assurance "as low that the releases as is reasonably achievable". of radioactive materials in liquid effluents will be l of 10 CFR 50.35a, General Design Criterion 60 of Appendix A to 10 CFR Part 50 i design objective given in Section 11.0 of Appendix I to 10 CFR Part 50. The specified limits governing the use of appropriate portions of the liquid radwaste treatment system I were specified as a suitable fraction of the dose design objectives set forth in Section II.A of Appendix 1, 10 CFR Part 50, for liquid effluents. . 2.4 RADI0 ACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION The radioactive gaseous effluent instrumentation is provided to monitor and control, as applicable, potential releases the releases of gaseousof radioactive effluents. The materials in gaseous effluents during actual or alarm / trip setpoints for these-instruments shall be calculated in accordance with the procedures in the 00CM to ensure that the alarm / trip will' occur prior to exceeding the limits of 10 CFR Part 20. The OPERABILITY Criteria 60, 63, and 64 of Appendix A to 10 CFR Part 50.and use of this ins 2.4.1 DOSE RATE This control is provided to ensure that the dose at any time at and beyond the SITE CFR Part 20 to UNRESTRICTED AREAS. BOUNDARY from gaseous effluents f the concentrations of 10 CFR Part 20. Appendix B. Table II, Column I.The annual d These limits ovide reasonable assurance that radioactive material discharged in gaseous effluents 11 not result in the exposure of a MEMBER OF THE PUBLIC in an tr f.ESTRICTED ARE within or outside the SITE BOUNDARY, to annual average concentrr; cons exceeding th specified in Appendix B Table II of 10 CFR Part 20 (10 CFR 20.4U6(b For MEMBERS OF THE PUBLIC who may at times be within the SITE BOUNDARY, thefactor occupanc)y(1)). for that MEMBER OF THE PUBLIC will usually be sufficiently low to compensate for any increase in [ the atmospheric diffusion factor for above that for the SITE B0VHDARY. Examples of calculations be given in thefor 00CM. such MEMBERS OF THE PUBLIC, with the appropriate occupancy factor 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 mre,ms/ year to the total body or less than or equal to 3000 mrems/ 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 mrems/ year. This specification applies to the release of radioactive materials in gaseous effluents from all reactors at the site. ESRfM MW i 1-13 I
%I
~
s;Pg 8 3/4 11-3od:74. - RWG
' DOSE RATE (Continued)-
The required detection capability for radioactive materials in gaseous waste samples are tabulated in terms of the Ic.er limits of detection (LLDs). Detailed discussion of the LLD, and other annually), detection Currie, L. A.,limits can be found in HASL Procedures Manual, HASL-300 (revised
- Application to Radiochemistry," " Limits for Qualitative Anal. Chem. 40,Detection and Quantitative Oetiermination 586-93 (1968), and Hartwell, J. K.,
" Detection Limits for Radioanalytical Counting Techniques." Atlantic Richfield Hanford Company, Report (ARH-SA-215 (June 1975).
- 2.4.2 DOSE - NOBLE GASES k
IV.AThis control is of Appendix 1, provided 10 CFR Part to implement the requirements of Sections 11.B, Ill.A, and
- 50. The control implements the guides set forth in Section 11.8 of Appendix 1.
The ACTION statements provide the required operating flexibility and at the same time implement the guides set forth in Section IV.A of Appendix 1 to assure that the releases of radioactive material in gaseous effluents will be kept "as low as is reasonably achievable". The Surveillance Requirements implement the s requirements in Section !!!.A of Appendix I that conformance with the guides of Appendix ! be shoWn by calculational procedures based on appropriate pathways is unlikely to be substantially underestimated. The dose calculation established in the ODCM for calculating the doses due to the actual release rates of radioactive noble gases in gaseous effluentt are consistent with the methodology provided in Regulatory Guide 1.109,
" Calculation Purpose of Annual of Evaluating Compliance Doses withto10Man from CFR Part 50,Routine Appendix Releases of Reactor Effluents fo 1," Revision 1, October 1977 and Regulatory Guide 1.111. " Methods for Estimating Atmospheric Transport and r Dispersion of Gaseous Effluents in Routing Releases from Light-Water Cooled Reactors,"
Revision 1, July 1977 with site specific dispersion curves and deposition methodology. The ODCM equations provided for determining the air doses at and beyond the SITE BOUNDARY are based upon the historical average atmospheric conditions. 2.4.3 FORM DOSE - 10 DINE-131. 10 DINE-133. TRITIUM. AND RADIONUCLIDES IN PARTICUL ~ IV.AThis control is of Appendix 1, provided 10 CFR Part to implement
- 50. the requirements of Sections ll.C, Ill.A, and of Appendix 1. The controls are the guides set forth in Section II.C
- The ACTION statements provide the required operating flexibility and at the same time implement the guides set forth in Sectioq IV.A of Appendix l to assure that the releases ceasonably of radioactive materials in gaseous effluents will be kept "as low as is achievable." The 00CM calculational methods specified in the Surveillance Requirements implement the requirements in Section Ill.A of Appendix 1 that conformance with the guides of Appendix 1 be shown by calculational procedures based on models and data, such that the cetual exposure of a MEMBER OF THE PUBLIC through appropriate pathways H . W 4#o 1-14 h I WI
----musiimm
~
birg o J/4 11-400:/4. - RwG e DOSE-10 DINE-131. 10 DINE-133, TRITIUM, AND RADIONUCLIOES IN PARTICULATE FORM (Continued) is unlikely to be substantially underestimated. The 00CM calculational methods for calculating the doses due to the actual release rates of the subject materials are ; consistent with the methodology provided in Regulatory Guide 1.109, " Calculation of Annual Doses to Man from Routine Releases of Reactor Effluents for the Purpose of Evaluating Compliance with 10 CFR Part 50, Appendix 1," 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 with site specific dispersion curves and deposition methodology. These equations also provide for determining the actual doses based upon the historical average atmospheric conditions. The release rate specifications for iodine-131, iodine-133, tritium, and radionuclides in particulate form with half-lives greater than 8 days are dependent'on the existing radionuclide pathways to man in areas at and beyond the SITE BOUNDARY. The pathways which were examined in the development of these calculations were: (1) individual inhalation of airborne radionuclides,~(2) deposition of radionuclides onto green leafy vegetation with subsequent consumption by man, (3) deposition onto grassy areas where milk animals and meat-producing animals graze with consumption of the milk and meat by man, and (4) deposition on the ground with subsequent exposure of man. 2.4.4 VENTILATION EXHAUST TREATMENT SYSTEM The requirement that the appropriate portions of this system be used, when specified, provides reasonable assurance that the releases of radioactive materials in gaseous effluents will be kept "as low as is reasonable achievable." This control implements the requirements of 10 CFR 50.36a, General Design Criterion 60 of Appendix A to 10 CFR Part 50, and the design objectives given in Section 11.D of Appendix I to 10 CFR Part 50. The-specified limits governing the use of appropriate portions of the systems were specified as a suitable fraction of the dose design objectives set forth in Section II.B and II.C of Appendix I, 10 CFR Part 50, for gaseous effluents. 2.4.5 VENTING OR PURGING This control provides reasonable assurance that releases from drywell purging operations AREAS. will not exceed the annual dose limits of 10 CFR Part 20 for UNRESTRICTED 2.4.6 TOTAL DOSE ' This control is provided to meet the dose limitations of 40 CFR Part 190 that have been incorporated into 10 CFR Part 20 by 46 CFR 18525. The control requires the the preparation and submittal of a Special Report whenever the calculated doses from plant radioactive effluents exceed twice the design objective doses of Appendix I. For sites containing up to four reactors, it is highly unlikely that the resultant dose to a MEMBER OF THE PUBLIC will exceed the dose, limits of 40 CFR Part 190 if the individual reactors remain within the reporting requirement level. ESP.30 WF I -, 1
stPg B 3/4 11-Sod:74.- RWG 2.4.6 TOTAL DOSE (Continued) L The Special Report will describe a course of action that should result in the limitation of the annual dose to a member of the publi.c to within the 40 CFR Part 190 limits. For the purposes of the Special Repo' r t, it s may be assumed that the dose commitment to the MEMBER OF THE PUBLIC from other uranium fuel cycle sources is negligible, with the exception that dose contributions from other nuclear fuel cycle facilities at the same site or within a radius of 5 miles must be considered. If the dose to any MEMBER OF THE PUBLIC is estimated to exceed the requirements of 40
- CFR'Part 190, the Special Report with a request for a variance (provided ,
i the release conditions resulting in violation of 40 CFR Part 190 have not already been corrected), in accordance with the provisions of 40 CFR 190.11 and 10 CFR 20.405c, is considered to be a timely request and fulfills the requirements of 40 CFR Part 190 until NRC staff action is completed. An individual is not considered a MEMBER OF THE PUBLIC during'any period in which he/she is engaged in carrying out any operation that is part of the nuclear fuel cycle. 2.5 RADIOLOGICAL ENVIROMENTAL MONITORING PROGRAM The radiological environmental monitoring program required oy this control provides representative measurements of radiation and of radioactive materials in those exposure pathways and for those radionuclides that lead to the highest potential radiation exposures of MEMBER OF THE PUBLIC resulting from the station operation. This monitoring program implements Section IV.B.2 of Appendix I to 10 CFR Part 50 and thereby supplements the radiological effluent monitoring program by verifying that the measurable concentrations of radioactive materials and levels of radiation are not higher than expected on the basis of the effluent measurements and modeling of the environmental ~ exposure pathways. The initially specified monitoring program will be effective for at least the first 3 years of commercial operation. Following this operational period, program changes may be initiated based on experience. The required detection capabilities for environmental sample analyses are tabulated in terms of the lower limits of detection The LL0s required by Table-4.12.1-1 are considered optimum for rou(LLDs). tine environmental measurements in industrial laboratories.It should be recognized that the LLD is defined as an a priori (before the fact) limit representing the capability of a measurement system and not an a_ posteriori (after the fact) limit for a particular measurement. Octailed discussion of the LLO, and other detection limits, can be found in HASL Procedures Manual, HASL-300 (revised annually); Currie L. A.,
" Limits Application to for Qualitative Detection Radiochemistry" Anal. Chem.and Quantitative Determination -
- 40. 586-93 (1968h and Hartwell. J. K.. " Detection Limits for Radioanalytical .
Countino Techniques," 1975). Atlantic Richfield Hanford Company Report ARH-SA-215 (June Engr I-16 H. P. - Date Rev.
stPg B 3/4 12-lod:74 - ric 2.5.1 LAND USE CENSUS. This control is provide'd to ensure that changes in the use of areas at and beyond the SITE BOUNDARY are identified and that modifications to the monitoring program are made if required by the results of this census. The best information from the door-to-door survey, aerial survey or consulting with local agricultural 3 authorities or any combination of these methods shall.be used. This census satisfies the requirements of Section IV.B.3 of Appendix.I.to 10 CFR Part'50. Restricting the census to gardens of greater than 500 square feet 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 l 1.109 for consumption.by a child. To determine this minimum gcrden size, the following assumptions were used: (1) that 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/ square meter. 2.5.2 INTERLABORATORY COMPARISON PROGRAM The requirement for participation in an 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 reasonably valid for the purpose of Section IV.B.2 of Appendix ! to 10 CFR Part 50. Engr. H. P. Date Rev. I-17 l l l . l l 1 l l 1 j 4
-2.6~APPLICA8ILITYi i
1 2.6.1 Compliance with the controls contained in the succeeding controls section is required during the OPERATIONAL CONDITIONS or other conditions specified therein; except requirements thatbeupon shall met.failure to meet the controls , the associated ACTION 2.6.2 Noncompliance w'ith a control shall exist when the requirements of the control and associated ACTION requirements are not met within the specified time intervals. intervals, completion of the ACTION requirements is not required 2.6.3 There are no actions in'the ODCM which would require an. operational condition change. 2.6.4 'There are no restrictions on changing. operating conditions in any of the controls of the ODCM. i The associated bases from the LGS Technical Specifications applies to this section 1 Date 34 e/to Rev. # l 1-18 'i I l 1 1
APPLICABILITY- ' 9 SURVE!LLANCE ' REQUIREMENTS 2.6.5 Surveillance Requirements shall be met during the OPERATIONAL CONDITIONS or other conditions specified for individual controls unless otherw'ise stated in an individual Surveillance Requirement. 2.6.6 Each Surveillance Requirement shall be performed within the specified time-interval with: -
'a. A maximum allowable extension not to exceed 25% of the surveillance ,
interval, but
- b. The combined time interval for any 3 consecutive surveillance intervals shall not exceed 3.25 timet the_specified surveillance interval.
2.6.7 Failure to perform a Surveillance Requirement within the allowed
= surveillance interval defined by control 2.6.6, shall constitute noncompliance with the OPERABILITY requirements for a' control. The time limits of the ACTION requirements are applicable at the time it is identified that a Surveillance Riquirement has not been performed. The ACTION requirements may be delayed for up to 24 hours to permit the completion of the surveillance when the allowable outage time limits of the ACTION requirements are less than 24 hours. Surveillance - requirements do not have to be performed on inoperable equipment.
Engr H. P. Date o Rev. l , L I-19 1 4 i l
%T
stPg 3/1-3-73/odt?4 - RWG' ' l METEOROLOGICAL MONITORING INSTRUMENTATION l
. CONTROLS I
~
. *- 3.1- I The meteorological monitoring instrumentation channels shown in Table 13.1-1 shall be OPERABLE..
APPllCABILITY: At all times. - ACTION: a.- With one or more meteorological monitoring instrumentation channels ~ inoperable-for more than 7 days, prepare and-submit a Special Report to the Commission pursuant to LGS Technical Specification 6.9.2 within the-next 10 days outlining the cause of the malfunction and the plans for $ restoring the instrumentation to OPERABLE status. ' SURVEILLANCE REQUIREMENTS i 3.1.1. iath of the above required meteorological monitoring instrumentation channels shall be demonstrated OPERABLE by the performance of the CHANNEL CHECK and CHANNEL CALIBRATION operations at the frequencies shown in Table 13.1-2. Engr. H. P. Date Rev. l-20 I 1 p 1 .
a.rw ai, a-i joa:/4 .LgLu'~' '~ ~- ' j TABLE 13.1 1- , METEOROLOGICAL MONITORING INSTRUMENTATION' i i i MINIMUM INSTRUMEN's Tower 1 . Tower '2 - (Primary) IBackup) INSTRUMENTS OPERABLE
,1. Wind Speed ,
'a. Elevation 1 30 feet or 159 feet . 1,_
- b. Elevation 2 175 feet or 304 feet _1 ;
- 2. Wind Direction !
- a. Elevation 1 30 feet or 159 feet 1
- b. Elevation 2 ~
175~ feet' or 304 feet 1
- 3. '. Air Temperature Difference-
- a. Elevations 266 feet- 300 feet.
'26 feet or 26 feet 1 i
i NOTE: ; The meteorological towers shall be located as shown on Figure 13.1-1. Engr.
.H.P.f -
Date-Rev. ,
, i I-21
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METEOROLOGICAL MONITORING INSTRUMENTATION SURVE I
-1 l
INSTRUMENT CHANNEL CHANNEL I
, CHECK
_ CALIBRATION
-1. Wind Speed .
Sa. Elevationl'(TowerILandTower2) 0- - SA ,
'b.
Elevation'2(TowerIandTower2) D SA 2.-' Wind Direction ! a. Elevation'l.(Tower 1 and Tower 2) D -SA-
,'b. . Elevation 2 (Tower 1 and Tower l2) D 'SA 3.; Air Temperature Difference-
~
- a. . Elevations 266 - l?6: f t (Tower 1) .D. 'SA
- b. Elevations 300 26-ft.(Tower 2)- D' SA:
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I I l Engr. H. P. . Date- S
. Rev. pi 1-22
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SIPg 3/4 3-98/cd 74 - RWG , RADI0 ACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTATION' CONTROLS
-3.2.1 In accordance with LGS TS 6.8.4.d.1, the radioactive liquid effluent monitoring instrumentation channels shown in Table 13.2-1 shall be OPERABLE with -
their alarm / trip setpoints set to. ensure that the limits of Control 3.2.2 are not exceeded. The alarm / trip setpoints* of these channels shall be determined ' and adjusted in accordance with the methodology and parameters in the OFFSITE DOSECALCULATIONMANUAL(ODCM).
' APPLICABILITY: At all times.
ACTION:
- a. With a radioactive liquid effluent monitoring instrumentation channel alarm / trip setpoint less conservative than required by the above
- control, immediately suspend the release of radioactive liquid effluents monitored by the affected channel, or declare the channel inoperable.-
- b. With less than the minimum number of radioactive liquid affh tent monitoring instrumentation channels OPERABLE, take the ACTION shown in Table 13.2-1. Restore the inoperable instrumentation to OPERABLE status within the time'specified in the ACTION or explain in the next Semiannual Radioactive Effluent Release Report'why this inoperability was not corrected within the time specified.
SURVEILLANCE REQUIREMENTS 3.2.1.1- Each radioactive liquid effluent moni'toring 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 13.2-2. Excluding the flow rate measuring devices which are not determined and adjusted in accordance with,the 00CM. Engr.h H.P. E . l'M 4 " l I-24 . l m, *
,, _. - - . , , , _ ~ _
. RADIDACTIVE L10010 EFFLUENT MONITORING-INSTRUMENTATION: o-MINIMUM I , CHANNELS-INSTRUMENT?
! OPERABLE LACTION
- 1. GROSS RADI0 ACTIVITY MONITORS PROVIDING, l
AUTOMATIC TERMINATION 0F RELEASE '
- a. Liquid Radwaste EffluentLLine 1 100
. b .' RHR. Service Water System Effluent Line 1/ loop 101
- 2. ) GROSS RADIOACTIVITY MONITORS NOT
PROVIDING AUTOMATIC TERMINATION' P 0F RELEASE
.a._ Service Water System Effluent Line 1 ~101 3.- FLOW RATE MEASUREMENT DEVICES l
- a. Liqdid Radwaste Effluent Line' t 1 102 I
- b. Discharge Line i
- 1. 102' -i ACTION' STATEMENTS : t a
ACTION 100 - With the number of channels OPERABLE less than required by thee Minimum Channels OPERABLE requirement; effluent releases may. , continue release: for..up to 14 days provided that prior-to initiating a. ; i a. At least two independent samples ate analyzed in accordance with Table _13.2-3, and '
',i b.
At least two technically. qualified members of the facility staff independently verify the release rate-calculations and. discharge line valving;'
-- t Otherwise, pathway.
suspend release of' radioactive effluents via this ACTION 101 - With the number of channels OPERABLE'less than required by-the- i Minimum Channels OPERABLE. requirement, effluent releases via this
-pathway may continue for up to 30 days provided that, at least once per 8 hours, grab samples are collected and analyzed-for gross radioactivity'(beta or gama). ' Beta-is analyzed at a limit of detection of at least 1N7 microcurie /mL. Gama is analyzed at a limit of detec, tion of at.least SN7 microcurie /ml. _} '
ACTION 102 - With the number of channels OPERABLE less 'outred by the Minimum Channels OPERABLE requirement, ei ' tases via this pathway may continue for up to 30 days pr flow rate is-estimated at-least once per 4 hours duri releases. Pump curves generated in situ may be used to flow. Engr. H. P. 1-25 s Date o Rev. I'
]
b%
s;Pg 3/4 3-101/od:74 - 4 - , r. TABLE 13.2-2 RADI0 ACTIVE LIQUID EFFLUENT MONITORING INSTRUMENTA INSTRUMENT CHANNEL SOURCE
-CHAhMEL-CHECK CHANNEL _ TUNCTIONAL
- CHECK
_ CALIBRATION TEST 1. GROSS RADI0 ACTIVITY MONITORS PROVIDING AUTOMATIC TERMINATION OF RELEASE
- a. Liquid Radwaste Effluent Line .
P. P
- b. R(3) .Q(1)
RHR Service Mater System Effluent Line - D M
- 2. R(3)- Q(1)
GROSS-RADI0 ACTIVITY MONITORS NOT PROVIDING-AUTOMATIC TERMINATION OF RELEASE i a. Service Water System Effluent Line ! D. M ! R(3) Q(2) 3. FLOW RATE MEASUREMENT DEVICES
- a. Liquid Radwaste Effluent Line
.D(4) N.A. R'
- b. 'Q.
Discharge Line
- 0(4) M.A. R. Q l
i l . l s Engr.
.H. P. -
Date G o ! Rev._ fr'
-I ~
, ~,..- . , , , , .
. . ~ . ,..-.n , .. u - ,n .-_ . , , , , , -_
7 _ _
a i TABLE 13.2-2 (Continv'ed) ' V TABLE NOTATIONS s _. (1) The'~ CHANNEL TUNCTIONAL TEST shall also demonstrate that automatic . isolation of of.this pathway the following ar.dexists: conditions control room alarm annunciation occur if any Y
- 1. ~
Instrument indicates measured levels above'the alarm / trip setpoin't.
- 2. Circuit failure.
3. Instrument indicates a downscale failure. ( (2) The CHANNEL FUNCTIONAL TEST shall'also demonstrate that controllroom annunciation occurs if any of the following. conditions exists:
. f
- 1. -Instrument indicates measured levels above the alarm setpoint.
- 2. Circuit failure.
3. Instrument indicates a'downscale failure. (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 HIST. These standards shall permit calibrating the system over-its intended l re.nge.of energy and measurement range. For subsequent CHANNEL ! CALIBRATION, sources that have been relhted to.the initial calibration shall be used. (4) CHANNEL CHECK shall consist of verifying; indication of flow during periods of release. CHANNEL CHECK _shal14 be made,at least once per 24 hours on days on which continuous, periodic, or batch releases are made. Engr., Tid i H. P.. 1-27' 'Date o ! Rev. ,
. t t9
s;Pg'3/4 11-1/od 74 - RWG CONCENTRATION CON 1ROLS 3.2.2 In accordance with LGS TS 6.8.4.d.2 and 3, the concentration of i-radioactive material released in liquid effluents to UNRESTRICTED AREAS (see Figure 12.2-la,b) shall be limited to the concentrations specified in 10 CFR Part 20, Appendix B. Table II, Column 2 for radionuclides other than dissolved or entrained nobles gases. Fo shallbelimitedto2x10g.dissolvedorentrainednoblegases,theconcentration microcuries/ml total activity. - , l APPLICABILITY,: At all times. ACTION: With the concentration of radioactive material released in liquid effluents to UNRESTRICTED AREAS exceeding the above limits, inmediately restore the concentration to w w in the above limits. SURVEILLANCE REQUIREMENTS l 3.2.2.1 Radioactive liquid wastes shall be sampled and analyzed according to the sampling and analysis program of Table 13.2-3. 3.2.2.2 The results of the radioactivity analyses shall be used in accordance with the methodology and parameters in the ODCM to assure that the concentrations at the point of release are maintained within the limits of Control 3.2.2. 1 Engr. , H. P. I Date jp o Rev. ':-
, , I-28 l
l 1 1
==
5%P9 3/4 II'2/'d 74 'oNWO RADI0 ACTIVE L10VID WASTE SAMPLING AND ANALYSIS PROGRAM
. LOWER LIMIT MINIMUM TYPE OF ,, Ll0U10 RELEASE SAMPLING ANALYSIS ACTIVITY OFDETEC}!ON (LLO)
TYPE FREQUENCY ! FREQUENCY ANALYS!$ (uCi/ML) l A.s Batch Waste P P Principal Gamma 5x10-7 ; Release Each Batch Each Batch Emitters C Tanksb I-131 1x10-6 l
- 1. Floor Drain P M Dissolved and 1x10-5 ,
Sample Tank One Batch /M Entrained Gases No. 2 (Gama [mitters)
- 2. Laundry P M H-3 Drain Sample 1x10-5 Each Batch Composite d lank Gross Alpha .1x10*7 P Q Sr-B9, Sr-90 5x10-8 ;
Each Batch Composite d - Fe-55 1x10-6 B. Continuogs W W Release PrincipagGamma 5x10'7 Grab Sample Emitters > a 1-131 -1x10-6
- 1. RHR Ser" ice W W Water $ystem Dissolved and 1x10-5 Gr&b Sample Entrained Gases Eff iwat Line7 (Gama Emitters)
- 2. Service Water W M H-3 System 1x10-5 Grab Sample Composited Effluent Gross Alpha 1x10'7 Line f i W Q Sr-89 Sr-90 5x10-8 ;
- Grab Sample Composite d Fe-55 1x10-6 Frgr._-A4R v
l-29
s;Ig$/411-3/cdr74.Rwc I TABLE 13.?-3(Continued) TABLENOTAT10Q "The LLO is defined, for purposes of these controls, as the smallest concentration of radioactive material in a sample that will yield a net count, above system background, that will be detected with 95% probability with only 5% probability signal. of falsely concluding that a blank o',servation represents a "real" For a particular measurement system, which may include radiochemical
, separation: ,
4.66s
~
LLO E *= V **2.22
* *x-""106' * * * *
- b ~ ~ '". 'y~ ~ ~. ~ e~x~ p~ ~
Where: LLOunit per is mass the aororiori lower limit of detection as defined above (as microcuries volume), sb is the standard deviation of the background counting rate or of the counting rate of a blank sample as appropriate (as courts per minute), E is the counting efficiency, as counts per disintegration, V is the sample size, in units of mass or volume, 2.22 x 106 is the number of disintegrations per minute per microcurie, Y is the fractional radiochemical yield, when a' Picable, A is the radioactive decay constant for the pc ':cular radionuclide, and a t for the plant effluents is the elapsed time between the midpoint of sample collection and time of counting. Typical values of E. V, Y, and 6t should be used in calculation. l j limit representing the capability of a measurement system and I potteriori (after the fact) limit for a particular measurement. Engr. 1-30 H. P. Date c Rev. i I e l' a , . . - - . - , - , , , . -
stPg 3/4 11-4/od874 - RWG l TABLE 13.P-3(Continued) TABtE NOTATION $ b . 1 2
*- A batch release is the discharge of liquid wastes of a discrete volume.
Prior to sampling for analyses each batch shall be isolated, and then ! thoroughly mixed to assure repr,esentative sampling. I i . ! C ~ The principal gama emitters for which the LLD specification applies include' 'l the following Cs-137, radionuclides: Ce-141, and Ce-144. Mn-54, Fe-59, Co-58, Co-60, 2n-65, Mo-99, Cs-134, l This list does not mean that only these nuclides s are to be considered. Other gama peaks that are identifiable, together with ' those of the above nuclides, shall also be analyzed and reported in the Semiannual Radioactive Effluent Release Report pursuant to Control 3.6. i d A composite sample is one in which the quantity of liquid sampled is proportional to the quantity of. liquid waste dischargeo and in which the method of sampling employed results in a specimen that is representative of the liquids released. i
- A continuous release is the discharge of liquid wastes of a nondiscrete '
- volume, e.g., from a volume of a system that has an input flow during the continuous release.
I l Whenever effluent releases are in excess of the monitor's setpoint. { Engr.
' H. P.
. -31 Date a
'o Rev. .
i
.q $
b 49
,-.--._,r,. , -.,.-w-,_ _.w..c- y. _ _ , , ,. - . , -. .* -
s%Pg 3/4 11-5/od:74 i DOSE
\
CONTROLS ! I s 3.2.3 In accordance with LGS TS 6.8.4.d 4 and 5, the dose or dose commitment to a MEMBER OF THE PUBLIC from radioactive materials in liquid effluents released from the site to UNRESTRICTED AREAS (See Figure 12.2-la) shall be limited:
\
'a. During any calendar quarter to less than or equal to 3 mrems to the total body and to less than or equal to 10 mrems to any organ, and
- b. During any calendar year to less than or equal to 6 mrems to the total body and to 1tss than or equal to 20 mrems to any organ. "
APPLICABILITY: At all times. A*. ; ION :
- a. With the calculated dose from the release of radioactive materials in liquid effluents exceeding any of the above limits, prepare and submit to the Commission within 30 days, pursuant to Technical Specification 6.9.2, aSpecialReportwhichidentifiesthecause(s)forexceedingthelimit(s) and defines the corrective actions that have been taken to reduce the releases and the presosed Corrective actions to be taken to assure that subsequent releases will be in compliance with the above limits. This Special Report shall also include the radiological impact on finished drinking water supplies at the nearest downstream drinking water source.
SURVEILLANCE REQUIREMENTS 3.2.3.1 Cumulative dose contributions from liquid efflue.'ts fne the current calendar quarter and the current calendar year shal( be determined in accordance with the methodology and parameters in the ODCM at ' east once per 31 days. l Engr. G H. P. 1-32 Date O Rey, 1 i W - 1
s;Pg 3/4 11-6/od:74 - RWG L10VID RADWASTE TREATMENT SYSTEM CONTROLS 3.2.4 In accordance with LGS TS 6.8.4.d.6. the liquid radwaste trestment system shall be OPERABLE anc appropriate portions of the system shall be used to reduce the radioactive materials in liquid waste prior to their discharge when the projected doses due to the liquid effluent, from the site, to UNRESTRICTED AREAS (see Figure 12.2-la) would exceed 0.06 mrem to the total body or 0.2. mrem to any organ in a 31-day period. APPLICABILITY: At all times. ACTION:
- a. With radioactive liquid waste being discharged without treatment and in excess of the above limits, prepare and submit to the Commission within
, 30 days pursuant to Technical Specification 6.9.2 a Special Report which includes the following information:
- 1. Explanation of what liquid radwaste was being discharged without treatment, identification of any inoperable equipment or subsystems, and the reason for the inoperability,
- 2. Action (s)takentorestoretheinoperableequipmenttoOPERABLE status, and
- 3. Summary description of action (s) taken to prevent a recurrence.
SURVEILLANCE REQUIREMENTS 3.2.4.1 Doses due to liquid releases from the site to UNRESTRICTED AREAS shall be projected at least once per 31 days in accordance with the methodology and parameters in the ODCM. 4.2.4.2 The liquid radwaste treatment system shall be demonstrated OPERABLE by meeting Controls 3.2.2 and 3.2.3. Engr.7 H. P. 1-33 Date fo Rev.
.> 9
- s;Pg 3/4 3-103/odg74 - RWG RADICACTIVE GASEOUS EFFLUENT MON!TORING INSTRUMENTATION CONTROLS 3.3.1 In accordance with LGS TS 6.8.4.d.l. the radioactive gaseous effluent monitoring instrumentation channels shonn in Table 13.3-1 shall be OPERABLE with their alarm / trip setpoints set to ensure that the limits of Control 3.3.2 are not exceeded. The alarm / trip setpoints of the applicable channels shall be determined in accordance with the methodology and parameters in the 00CM.
- i APPLICABILITY: As shown in Table 13.3 1 l
ACTION:
- a. With a radioactive gaseous effluent monitoring instrumentation channel
- alarm / trip setpoint less conservative than required by the above i Control, imediately suspend the release of radioactive gaseous effluents monitored by the affected channel or declare the channel inoperable.
- b. With less than the minimum number of radioactive gaseous effluent monitoring instrumentation channels OPERABLE, take the ACTION shown in Table 13.3-1. Restore the inoperable instrumentation to OPERABLE status within the time specified in the ACTION or explain why this inoperability was not corrected in a timely manner in the next Semiannual Radioactive Effluent Release Report.
i l SURVEILLANCE REQUIREMENTS l 3.3.1.1 Each radioactive gaseous effluent monitoring instrumentation channel shall be demonstrated OPERABLE by performance of the CHANNEL CHECK. SOURCE CHECK, CHANNEL CAllBRATION, and CHANNEL FUNCTIONAL TEST operations at the frequencies shown in Table 13.3-2. Engr.mN 1-34 t o 6 b%
. TA8LE 13.3-1 RADI0 ACTIVE GASEOUS EFFLUENT MONITORING INSTRUMENTATION MINISEM CHANNELS INSTRUMENT ,
OPERA 8tE APPLICABILITY ACTION ' j 1. SOUTH STACK EFFLUENT MONITORING SYSTEM ! i
- a. Noble Gas Activity Monitor
- 1 , 111
- b. Iodine Sampler
- l 1 112
- c. Particulate Sampler
- 1 112 ' l
- d. Effluent System Flow Rate Monitor
- 1 113 1
- e. Sampler Flow Rate Monitor.
- i 1 113
- 2. NORTH STACK EFFLUENT MONITORING SYSTEM I
1
- a. Noble Gas Activity Monitor 1
- 114
- b. Iodine Sampler 1 *
, 112
- c. Particulate Sampler 1
- 112
, d. Effluent System flow Rate Monitor i 1 * ' 113
- e. Sampler Flow Rate Monitor t
1
- 113 1
1 's Engr.
.1-35 H. P.
Dr** : I
s;Pg 3/4 3-105/od:74 - RWG TABLE 13.3-1 (continued) 4 j s RADIDACTIVE' GASEOUS EFFLUENT MONITORING INSTRUMENTATION 4 INSTRUMENT MINIMLM CHANNELS 4 _ OPERABLE APPLICABILITY ACTION
- 3. HOT MAINTENANCE SHOP VENTILATION EXHAUST RADIATION MONITOR
- a. Iodine Sampler
- 1 **
112
- b. Particulate Sampler 1 **
i 112
- c. Effluent System Flow Rate Monitor 1 **
113
- d. Sampler flow Rate Monitor 1 **
113 i e S
'* II"';:M ,
22 V' . e i B
~
_ _ _ _ _ _ _ _ _ ______:___u____________._
- -- ' ~~~ ^ ~ ~ ~ ~ ~ . . _ _ _ _ _ . . --- ~
stPg 3/4 3-106/ tdt?4 - RWG . TABLE 13.3-1 (Continued) TABLE NOTATIONS s
- At t11 times. :
l-
** During operation of the hot maintenance shop ventilation exhaust system.
. ACTION STATEMENTS _ ,
ACTION 111 - i With the number of channels OPERABLE less than required by the i Minimum Channels OPERABLE requirement, effluent releases via this pathway may continue for up to 30 days provided grab samples are taken at gross least once activity withinper 24Bhours. hours and these samples are analyzed for I ACTION 112 - With the number of channels OPERABLE less than required by the Minimum Channels OPERABLE requirement, effluent releases via this pathway may continue for up to 30 days provided samples are t continuously collected with auxiliary sampling equipment as required in Table 13.3-3 ACTION 113 - With the number of channels OPERABLE less than required by the Minimum Channels OPERABLE requirement, effluent releases via this pathway may continue for up to 30 days provided the flow rate is estimated at least once per 4 hours. ACTION 114 - With the number of channels OPERABLE less than required by the Minimum Channels OPERABLE requirement, effluent releases via this pathway may continue for up to 30 days provided grab samples are taken at least once per B hours and.these samples are analyzed for i gross activity within 24 hours and provided the mechanical vacuum pumps are not operated. Engr. 1-37
. H. P.
Date Rev. . . . _ e 9
s;Pg 3/4 3-107/od:74 - RWG TABLE 13.3-2 RADIDACTIVE GASEOUS EFftDENT MONITORING INSTRUMENTATION SURVEILLANCE REQUIREMENTS s CHANNEL MODES IN INilCH' CHANNEL SOURCE CHANNEL
- NSTRUNENT FUNCTIONAL SURVEILLANCE CHECK CHECK CALIBRATION TEST 15 REQUIRE 0 '
- 1. SOUTH STACK Effluent MONITORING SYSTEM '
- a. Noble Gas Activity Monitor D M R(2) Q(1) *
. b. iodine Sampler W(3) N.A. N.A. N.A. *
- c. Particulate Sampler
- W(3) N.A. N.A. N.A.
- I
- d. Effluent System flow Rate Monitor ;
D N.A. -R Q *
's. Sampler flow Rate Monitor D N.A. R Q * '
?. NORTH STACK EfftDENT MON 110 RING SYSTEM ,
- a. Noble Gas Activity Monitor D M
! R(2) Q(1) *
- b. Iodine Sampler W(3) N.A. M.A. N.A. *
- c. Particulats Sampler W(3) N.A. N.A. N.A.
- d.
Effluent System flow Rate Monitor D N.A. R Q~ *
- e. Sampler flow Rate Monitor D N.A. R Q
- i e
Engr.I'd
- I'30 H. P.
Date o i Rev.
l TABLE 13.3-2 (Continued) c RADI0 ACTIVE GASE0CS EFFLUENT MONITORielG INSTRISENTATION SURVEILLANCE REQUIREMENTS \~ ' CHANNEL MODES IN lallCN CHAINIEL SOURCE CHANNEL FUNCTIONAL SURVEILLANCE INSTRUMENT CHECK CHECK CALIBRATICII TEST IS REQUIRES l
- 3. NOT MAINTENANCE SHOP VENTILATION -
EXHAUST RADIATION M00lITOR i 0. Iodine Sampler; W(3) II. A. N.A. N.A. **
- b. Particulate Sampler N.A. . N.A. **
W(3) M.A. l c. Effluent System flow Rate Monitor D N.A. R Q
- d. Sampler Flow Rate Monitor D II.A. R **
Q . I 7 Engr. 7/8 I-39 H. P. Date Rev. i 4 4
sjPg 3/4 3-109/od374 - RWG o TABLE 13.3-2(Continued) TABLE NOTATIONS
- At all times.
** During operation of the hot maintenance shop ventilation exhaust system.
(1), The CHANNEL FUNCTIONAL TEST shall also demonstrate that control room alarm ' annunciation occurs if any of the following conditions exists:- , 1. Instrument indicates measured levels above the alarm / trip setpoint.
- 2. Circuit failure.
- 3. Instrument indicates a downscale failure, 4 i
, Instrument controls not set in operate mode. 1 (2) The initial CHANNEL CALIBRATION shall be performed using one or more of ths. reference standards certified by the National Institute of Standards i andTesting(NIST)orusingstandardsthathavebeenobtainedfrom suppliers that participate in measurement assurance activities with NIST. These standards shall permit calibrating the system over its intended t range of energy and measurement range. For subsequent CHANNEL l i CALIBRATION, sources that have been related to the initial calibration shall be used. i ! (3) e iodine artridges and particulate filters will be changed at least gno;.g 1-e. W'. $
)
l
. s;Pg 3/4 11-8/od 74 - RWG *'
GASEOUS EFFLUENT $ OOSE RATE CONTROLS . 3.3.2 In accordance with LGS TS 6.8.4.o.7 the dose rate due to radioactive materials released in gaseous effluents from the site to areas at or beyond the SITEBOUNDARY(seefigure12.2-14)shallbelimited~tothefollowingt ,
- a. For noble gases: Less than or equal to 500 mrems/yr to the total body and less than or equal to 3000 mress/yr to the skin, and
- 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 to 1500 mrems/yr to any organ, (Inhalationpathwaysonly.)
APPLICABILITY: At all times. ACTION:
- a. With the dose rate (s) exceeding the above limits, immediate'ly restore the release rate to within the above limits.
SURVEILLANCE REQUIREMENTS 3.3.2.1 The dose rate due to noble gases in gaseous effluents shall be determined to be within the above limits in accordance with the methodology and parameters of the ODCM. 3.3.2.2 The dose rate due to iodine-131, iodine-133, tritium, and all radionuclides in particulate form with half-lives greater than 8 days in gaseous effluents shall be determined to be within the above limits in accordance with the methodology and parameters of the 00CM by obtaining, representative samples and performing analyses in accordance with the sampling and analysis program specified in Table 13.3-3. Engr H. P. 1-41 Date i Rev. 1 b9 e v
grg J/g. . . . . _ _ _11-9/od-/0 - Ittd6. . . . ' 1ABLE 13.3-3 l i RADIDACTIVE GASEQUS WAS1E SAMPLllIG AND AllALYSIS PROGRAM ! Misteest LOWER LIMIT OF t SAfrLillE AIIALYSIS TVPE OF GASE0tsS RELEASE TYPE FREQUEIICY DETECTIGIS (LLB)* FREQUEIICY ACTIVITY AIIALYSIS
, (mC1/mL) L l
l P p A. Contalement Purge Each Purge Each Purge Principal Gamma Emitters **f
- _(Pretreatment) Grab I x 10-4 Sagle B. Ilorth Stack and 88 Mb Principal Gamma Emitters
- South Stack lx10-4 i Grab Sample -6 H-3 1x10 ;
1
/ . ,
C. Hot Maintenance Continuousd gc Shop Ventilation I-131 lx10-12 j Charcoal 1-133 lx10-10 , , Exhaust 8 and All
- Release Types gp in B Continuousd gc- Principal Gamma Emitters
- i lx10-II culate (I-131,Others) i .
Continuousd Q Gross Alpha , Composite Par- lx10-II
. tSculate Sagle i t Continuousd 0 S#-8I* Sr-90 lx10-II Composite Par-ticulate Sample S. All Release Types Continuousd Iloble Gas Listed in 8 above lloble Gases lx10-0 Monitor Gross Beta or Gamma
^ (Based on Xe-133)
'I m ,
, . , 5"';:9% '
. ate . ,o r Rev.
, s;Pg 3/4 11-10/od:74 - RWG .
TABLE 13.3-3 (C ntinued) TABLE NOTATIONS
)
aihe LLD is defined, for purposes of these Controls, as the smallest concentration of radioactive material in a sample that will yield a. net count,
'- above system background, that will be detected with 95% probability with only 5%
probability of falsely concluding that a blank observation represents a "real" signal. - for a particular measurement system (which may include radiochemical separation): ' 4.66s LLD = ---------------- b -------------- E
- V
- 2.22 x 10b-* Y ' exp (-Xat)
Where: LLDistheapriorilowerlimitofdetectionasdefinedabove(asmicrocuries
, perunitmassorvolume), ,
Sb is the standard deviation of the background counting rate or of the countingrateofablanksampleasappropriate(ascountsperminute). Eisthecountingefficiency(ascountsperdisintegration), V is the sample s4re (in units of mass or volume), 6 2.22 x 10 is the number of disintegrations per minute per microcurie, Yisthefractionalradiochemicalyield(whenapplicable), A is the radioactive decay constant for the particular radionuclide, and At is the elapsed time between midpoint of sample collection and time of counting (forplanteffluents,notenvironmentalsamples) The value of sb used in the calculation of the LLD for a detection system shall be based on the actual observed variance qf the background counting rate or of the counting rate of the blank samples (as appropriate) rather than on an unverified theoretically predicted variance. ! Typical values of E. V, Y, and & t shall be used in the calculation. ItshouldberecognizedthattheLLDisdefinedananapriori(beforethe fact)limitrepresentingthecapabilityofameasurementsystenandnotasan aposteriori(afterthefa'ct)limitforaparticularmeasurestat. Engr.4 H. P. i 1-43 Date > Rev. l l t> 9
., - . - - . .- - , , . . . . . . . - , _ , . ___..,m.-_. - _ , . _ . - . . - - , . - ~ . . . . , . .
...,.,1 .. 4m h -nru~ ',
TABLE 13.3-3(Continued) TABLE NOTATIONS I b , Sampling and analyses shall also be performed following shutdown, startup, or i a THERMAL hour period. POWER change exceeding 15% of the RATED THERMAL POWER within This requirement does not apply if DOSE EQUIVALENT I-131 concentration in the primary (1) analysis shows that the coolant has not increased more than a factor of 3; and (2) the main condenser offgas pre-treatment
,a factor of 3. radioactivity monitor shows that effluent activity has not inc c -
Samples shall be changed at least once per 7 days and analyses shall be ! completed within 48 hours after changing, or after removal from sampler. t Sampling shall also be performed at least once per 24 hours for at least 7 of RATED THERMAL POWER in 1 hour and analyses com changing. LLDs may be increased by a factor of 10. This requiremen coolanthasnotincreasedmorethanafactorof3;and(2)the
- monitor
- 3. shows that effluent activity has not increased more than a (2ctor of d
The ratio of the samp12 flow rate to the sampled stream flow rate shall be known for the time period covered by each dose or dose rate calculation made { in accordance with Controls 3.3.2, 3.3.3, and 3.3.4. t e The principal gamma emitters for which the LLD specification applies include the following radionuclides: Kr-87 Kr-88, Xe-133, Xe-133m, Xe-135, Xe-135m and Xe-138 for gaseous emissions and Mn-54, Fe 59. Co-58, Co 60, Zn-65, . 1-131, Cs-134 Cs-137, Ce-141 and Ce-144 for particulate emissions. This list does not mean that only these nuclides are to be considered. Other gamma peaks which are identifiable, together with those of the above nuclides, shall also bepursuant Report, analyzedtoand reported Control 3.6 in the Semiannual Radioactive Effluent Release f l Under the provisions of footnote e. above, only noble gases need to be considered. g , Required for the hot maintenance shop ventilation exhaust only during operation of the hot maintenance shop ventilation exhaust system. , Engr. I-44 H. P. Date Rev. ,J_, -
.m 9 -
i s;Pg 3/4 11-12/odt74 - RWG * ; DOSE - NDBLE GASES , CONTROLS 1 3.3.3 In accordance with LGS TS 6.8.4.d.5 and 8, the air dose due to noble
*- gases released in gaseous effluents, from the site to areas at and beyond the SITE BOUNDARY (see Figure 12.2-la) thall be limited to the following:
- a. During any calendar quarter: Less than or equal to 10 mrads for ;
3 radiation and 1655 than or equal to 20 mrads for beta radiation, gamma and
- b. During any calendar year: Less than or equal to 20 mrads for gamma radiation and less than or equal to 40 mrads for beta radiation, ,
APPLICABILITY: At all times. ACTION:
- a. With the calculated air dose from radioactive noble gases in gaseous effluents exceeding any of the above limits, prepare and submit to the .
Commission within 30 days, pursuant to Technical Specification 6.9.2, a SpecialReportwhichidentifiesthecause(s)forexceedingthelimit(s) and defines the correctivc 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 SURVEILLANCE REQUIREMENTS ' 3.3.3.1 Cumulative dose contributions for the current calendar quarter and current calendar year for noble gases shall be determined in accordance with the methodology and parameters in-the ODCM at least once per 31 days. e Engr. H. P. 1-45 Date Rev. , i
+
_ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ . _ - - - - - - ' - ~ ~ ~ ~
stPg 3/4 al-13/odg74 - RWG
- DOSE - 100!NE-133. TRIT!UM. AND RADIONUCLIOE5 IN PARTICULATE FORM ,
CONTROLS 3.3.4 In accordance with LGS TS 6.8.4.d.9, the dose to a MEM'BER'0F THE PUBLIC
from iodine-131, iodine-133, tritium, and all radionuclides in particulate form with half-lives greater than 8 days in gaseous effluents released, from the site to areas at and beyond the SITE BOUNDARY (see Figure 12.2-1a) shall be limited to the following: -
i
' a. During any calendar quarter: Less than or equal'to 15 mress to any organ i and,
- b. During any ca'endar year: Less than or equal to 30 mrems to any organ.
APPLICABILITY: At all times. ACTION:
, a. With the calculated dose from the release of iodine-131, iodine-133, tritium, and radionuclides in particulate form with half-lives greater than 8 days, in gaseous effluents exceeding any of the above limits.
- prepare and submit to the Commission within 30 days, pursuant to Technical Specification 6.9.2, a Special Report which identifies the cause(s)forexceedingthelimitanddefinesthecorrectiveactionsthat have been taken to reduce the releases and the proposed corrective actions to be taken tc assure that subsequent releases will be in compliance with the above limits.
?
SURVEILLANCE REQUIREMENTS 3.3.4.1 Cumulative dose contributions for the current calendar quarter and ' current calendar year for iodine-131, iodine-133, tritium, and radionuclides in particulate form with half-lives greater than 8 days shall be determined in ' accordance with the methodology and parameters in the 00CM at least once per 31 days. Engr. H. P. 1-44 Date Rev. ' 1 . l l 1 i
. .l ms
s;Pg 3/4 11-14/odt74 - RWG . VENTILATION EXHAUST TREATMENT SYSTEM , CONTROLS 3.3.5 In accordance with LGS TS 6.8.4.d.6 the VENTIi.ATION EXHAhST TREATMENT SYSTEM shall be OPERABLE and appropriate portions of the system shall be used to reduce radioactive materials in gaseous waste prior to their discharge when the projected doses due to gaseous effluent releases, from the site to areas at and , beyondtheSITEBOUNDARY(seeFigure12.2-1)whenaveragedover31dayswould exceed 0.6 mrem to any organ in a 31-day period. . , APPLICABILITY: At all times. ! ACTION:
- a. With gaseous waste being discharged without treatment, and in excess of '
the above limits, prepare and submit to the Comission within 30 days, pursuant to Technical Specification 6.9.2, a Specic1 Report which
, 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. l
- 2. Action (s) taken to restore the inoperable equipment to OPERABLE status, and '
- 3. Sumary description of action (s) taken to prevent a recurrence. '
i SURVEILLANCE REQUIREMENTS 3.3.5.1 Doses due to gaseous releases from the site to areas at and beyond the SITE boundary shall be projected at least once per 31 days in accordance with the methodology and parameters in the ODCM. 3.3.5.2 TheVENTILATIONEXHAUSTTREATMENTSYSTEhshallbedemonstrated OPERABLE by meeting Controls 3.3.2, 3.3.3 or 3.3.4. Engr.\ H. P. I-47 Date
, Rev.
e i
- a. , , . . . - - - . - - _,
s;Pg 3/4 ll-17/od 74 - RWG j VENTING OR PURGING * *
. l l
CONTROLS 3.3.6 In accordance with LGS TS 6.8.4.d.10, VENTING or PURGING of the Mark !! containment shall be through the standby gas treatment system. APPLICABILITY: Whenever the containment is vented or purged.* ACTION: I
- c. With the requirements of the above specification not satisfied, susp'end all VENTING and PURGING of the containment. ,
SURVEILLANCE REQUIREMENTS '
. t 3.3.6.1 The containment shall be determined to be aligned for VENTING or 4
PURGING through the standby gas treatment system within 4 hours prior to start of , and at least once per 12 hours during VENTING or PURGING of the containment. 3.3.6.2 Prior to use of the purge system through the stanaby gas treatment P system assure that: a. Both standby gas treatment system trains are OPERABLE whenever the purge system is in use, and b. Whenever the purge system is 1n use during OPERATIONAL CONDITION 1 or 2 or 3 only one of the standby gas treatment system trains may be used.
*Exceptfortheoneinch/twoinchventvalvestotheReactorEnclosure .
Ecuipment Compartment Exhaust Filters when used for contaiteent pressure control and nitrogen make-up operations. Engr. 1-48 H. P. Date o Rev. i
s;Pg 3/4 11 20/od874 - RWG RADIDACTIVE EFFLUENTS . i TOTAL DOSE I CONTROLS 1 3.3.7 In accordance with LGS TS 6.8.4.d.11, the annual (calendar year) dose or dose commitment to any MEMBER OF THE PUBLIC, due to releases of radioactivity and radiation, from uranium fuel cycle sources shall be limited to less than or equal l to 25 mrems to the total body or any organ, except the thyroid, which shall be ' limited to less than or equal to 75 mrems. ' APPLICABILITY: At all times. ACTION:
- a. With the calculated doses from the release of radioactive materials in liquid or gaseous effluents exceeding twice the limits of Control 3.2.3.a. 3.2.3.b., 3.3.3.a., 3.3.3.b., 3.3.4.a., or 3.3.4.b.,
- calculations shall be made including direct radiation contributions from the reactor units and from outside storage tanks to determine whether the above limits of Control 3.3.7 have been exceeded. If such is the case, prepare and submit to the Commission within 30 days, pursuant to Tech.
Specification 6.9.2, 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 schieving conformance with the above limits. This Special Report, as defined in 10 CFR 20.405c, shall include an analysis that estimates the radiatior.
exposure (dose) to a MEMBER OF THE PUBLIC from the uranium fuel cycle sources, including all effluent pathways and direct radiation, for the calendar year that includes the release (s) covered by this report. It , shall also describe levels of radiation and concentrations of radioactive material involved, and the cause of the exposure levels or-concentrations. Iftheestimateddose(s)exceedstheabovelimits,and if the release condition resulting in violation 40 CFR Part 190 has not already been corrected, the Special Report shall include a request for a
- variance in accordance with the provisions of 40 CFR Part 190. Submittat of the report is considered a timely request, and a variance is granted until staff action on the request is complete.
SURVEILLANCE REQUIREMENTS l- 3.3.7.1 Cumulative dose con determined in accordance with,tributions from liquid and gaseous effluents shall be Controls 3.2.3.1, 3.3.3.1, and 3.3.4.1, and in accordance with the methodology and parameters in the 00CM. 3.3.7.2 If the cumulative dose contributions exceed the limits defined in ' 3.3.7a, Cumulative dose contributions from direct radiation from unit operation ' shall be determined in accordance with the methodology and parameters in th DCM Part 11. Engr. ' H. P. 1-49 , Date o Rev. i ms
s;P9 3/412-1tdca 74 - RWCT 4
. RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM CONTROLS ,
3.4.1 in accordance with LGS )$ 6.8.4.f.1, the radiological environmental monitoring program shall be condu*ted as specified in Table 13.4-1. APPLitABILITY: At all times. - i ACTION a. With the radiological enviernmental monitoring program not being conducted as specified in Table 13.4-1, prepare and submit to the ! Commission, in the Annual Radiological Environmental Operating Report per Control 3.5, a description of the reasons for not conductin program as required and the plans for preventing a recurrence. g the
'b. With the level of radioactivity as the result of plant effluents in an environmental sampling medium at a specified location exceeding the j reporting levels of Table 13.4-2 when averaged over any calendar quarter, prepare and submit to the Commission within 30 days, pursuant to Technical Specification 6.9.2, a Special Report that identifies the cause(s) for exceeding the limit (s) and defines the corrective actions to be taken to reduce radioactive effluents so that the potential annual dose to a MEMBER OF THE PUBLIC is less than the calendar year limits of Controls 3.2.3, 3.3.3 and 3.3.4. When more than one of the radionuclides in Table 13.4-2 are detected in the sampling medium, this report shall be submitted if:
I concentration 4T) concentration (2) i
+
reporting level (1) reportinglevel(2) +
,..{1.0 When radionuclides other than those in Table 13.4-2 are detected and I are the result of plant effluents, this rt: port shall be submitted if the potential annual dose to a MEMBER OF THE PUBLIC is eqaal to or greater than the calendar year limits of Co4rols 3.2.3, 3.3.3, and 3.3.4.
This report is not required if the measured level of > radioactivity was not the result of plant effluents; however, in such an event, the condition shall be reported and described in the Annual Radiological Environmental Operating Report. O i 1 1-50 5"'E: % . Date Rev. e S
.h 1
-------,.-.+,-w,- . - - +.-
stPg3/4 12-2/odem 74 - RbG 1 RADIOLOGICAL ENVIRONMENTAL MONITORING , CONTROLS . t ACTION (Continued)
, c.
~
With milk or fresh leafy vegetable samples unavailable from one or more of the sample locations required by Table 13.4-1, identify locations for obtaining replacement samples and add them to the radiological environmentas monitoring program within 30 days. The specific locations from which temples were unavailable may then be deleted from i the monitoring program. Pursuant to. Technical Specification 6.14, t submit as a part of or concurrent with the Semiannual Radioactive Effluent Release Report, a complete, legible copy of the entire ODCM, - including a revised figure (s) and table for the 00CM reflecting the new location (s). SURVEILLANCE REQUIREMENTS ; P 3.4.1.1 The radiological environmental monitoring samples shall be collected l pursuant to Table 13.4-1 from the specific locations given in the table and figure (s) in the ODCM and shall be analyzed pursuant to the requirements of ; l Table 13.4-1, the detection capabilities required by Table 13.4-3. 6 s Engr H. P. 1-51 Date ! , , Rev. 1
)
l l i 4
'l 1
- _,.3.. .. ... __. - L.
TABLE 13.4-1 J RADIOLOGICAL ENVIR0l#1 ENTAL MONI10 RING PROGRAM NUMBER OF REPRESENTATIVE EXPOSURE PATHWAY SAMPLES AND SAMPLING AND AND/0R SAMPLE TYPE AND FREQUENCY
. SAMPLE LOCATIONS (a) s COLLECTION FREQUENCY OF ANALYSIS
- 1. DIRECT RADIATION (b) 40 routine monitoring stations
! At least Quarterly. Gamma dose at least either with two or more dosimeters quarterly. or with one instrument for i
, . measuring'and recording dose rate 1
~
continuously placed as follows-i (1) An inner ring of stations,
~ one in each meteorological sector, in the general area of
- i the SITE BOUNOARY: (2) An outer ,
ring of stations, one in each meteorological sector, in the 3-to-9-alle range from the site;- , (3) The balance of the stations placed in special' interest areas ' such as population centers, - nearby residences, schools, and , in 1 or 2 areas to serve as i control stations..
- 2. AIRBORNE Radiolodine and Samples from 5 locations:
Particulates Continuous sampler . Radiolodine Cannister:
- a. 3 samples from close to the operation with sample I-131 analysis weekly.
collection weekly, or 4 - 3' SITE BOUNDARY locations (in more frequently if i different sectors) of the required by dust Particulate Sampler: i highest calculated annual loading.C i ^ average groundlevel x/Q Gross beta radio
- b. I sample from the vicinity -
activity analysis
-community having one of the follow 1 highest calculated annual change;p filter highest groundlevel x/Q. Gamma isotopic analysis
- of composite (by location) at least quarterly.
Engr. T S 5 1-52 N. P. Date
Rev.
_ _ ~_ _ - _ _ _ _ _ _ _ _ _ _ _ _ _ - _ _ - _ _ _ = _ _ _ _
. _ . _ _ _ _ _ . _ _ _ . . _ ~ . _ _ _ . _. ._ _ . . . _. . . . _ .
_ ~ - - - - - _ _ i
~
TABLE 13.4-1 (Continued)
. ~ RADIOLOGICAL ENVIROl8 ENTAL MONITORING PROGRAM
( t i NtMBER OF' REPRESENTATIVE XPOSURE PATHWAY SAMPLES AND } AN0/OR SAMPLE SAMPLING AND TYPE AND FRE00ENCY SAMPLE LOCATIONS (a) 2, COLLECTION FREQUENCY OF ANALYSIS AIR 80RNE (Continued) 1 sample from a control loca-tion, as for example 15-30 km distant and in the least pre- ' valent wind direction.
- 3. WATERBORNE ,
a.'Surfacef I sample upstream
- 1 I sample downstream Composite sampi Gamma isotopic analysis'
- 1-monthperiod.gover monthly. Composite for i b. Ground Samples from 1 or 2 sources tritium analysis quarterly.
I Quarterly. Gamma isotopic
- and tritium only if likely to be affected.h
- c. Drinking 1. sample of each of 1 to 3 analysis quarterly.
of the nearest water supplies Monthly. (Composite) I-131 analysis on each i that could be affected by its composite when the dose discharge. calculated for the con-L sumption of the water i is greate I 3 sample from a control per year.{ than I area Composite
, location. for gross beta and gasuna 1sotopic analyses monthly. '
{ Composite for tritlum } d. Sediment I sample from downstream area analysis , quarterly. from with existing or potential -Semiannually. Gamma isotopic analysis' shoreline recreational value. semiannually. i Engr. , I-53 N. P. L . Date - i Rev. 4
~
s;Pg 3/4 12-Sodca:74 - RWG l TABLE 13.4-1 (Continued)
- - . RADIOLOGICAL ENVIRON 8 ENTAL MONITORING PROGRAM i d
NUMBER OF REPRESENTATIVE EXPOSURE PATindAY SAMPLES AND SAMPLING AND ! TYPE AND FREQUENCY AN0/OR SAMPLE SAMPLE LOCATIONS (a) COLLECTION FREQUENCY OF ANALYSIS
- 4. INGESTION ,
i
- a. Milk a. Samples from milking animals Semimonthly when ant- Gasuna isotopic" and 1-131 in 3 locations within 5 km mais are on pasture, analysis semimonthly when distance having the highest monthly at other times. animals are on pasture; dose potential. If there are monthly at other times.
none, then. I sample from allking
~
animals in each of 3 areas between 5- to 8-km distance where ' doses are calculated to be . greater than I arem per yr.I 1 sample from milking animals at . a ccntrol location (15-30 km 4 km distant and in the least prevalent wind direction).
- b. Fish and a. I sample of two recreationally Sample in season, or Gasuna isotopic' 1 Invertebrates important species in vicinity semiannually if they analysis on edible i of plant discharge area. are not seasonal. portions.
I sample of same species In i area not influenced by plant discharge. l . l, Engr.J/8 ' ! I-54 ~ at , t 4-9 1 l
- _ - - - . ~ . . -- . . ~ ~ - . - ._ ... .. .
p __ TABLE 13o4-1 (Continued) i - i RADIOLOGICAL ENVIR00 MENTAL MONITORING PROGRAM ; O j i NWWER OF REPRESENTATIVE EXPOSURE PATHWAY i SAMPLES AND SAMPLING "JIO TYPE AND FREQUENCY AND/OR SAMPLE SAMPLE LOCATIONS (a) COLLECTION i1EQUENCY OF ANALYSIS !
- 4. INGESTI0h (Continued)
- c. Food Products Samples of 3 different Monthly when available, Gamma isotopic' and kinds of broad leaf if allk sempling is 1-131 analysis.
vegetation grown nearest not performed. i i each of two different offsite ; locations of highest . predicted annual average ground level D/Q if slik i sampling is not performed. ~ I sample of each of the similar Monthly when available, Gamma isotopic' and ' broad leaf vegetation grown if milk sampling is I-131 analysis. > 15-30 km distant in the least not performed. orevalent wind direction if i alik sampling is not performed.
- Engr. i N. P.
Date i Rev. 4 I-55
- I
s;Pg 3/4 12 7odca,:74 ,- RWG i RADIOLOGICAL ENVIRONMENTAL MONITORING : _ TABLE 13.4-1 (Continued) ! t TABLE NOTATIONS
)
a Specific parameters of distance and direction sector from'the centerline ! s of the-two reactors and additional description where pertinent, shall be provided figure (s) in forthe each ODCM. and every sample location in Table 13.4-1 in a table and 3 1 Deviations are permitted from the required sampling schedule if specimens are unobtainable due to hazardous Conditions, seasona. I unavh;16tility, malfunction of automatic sampling equipment and other legitimat
' reasons.
If specimens are unobtainable due to sampling equipment malfunction, everysampling next effort shallperiod. be made to Complete corrective action prior to the end of the I All deviations from the sampling schedule shall be l documented Control 3.5. in the Annual Radiological Environmental Operating Report pursuan! It is recognized that, at times, it may not be possible or practicable to continue to obtain samples of the media of choice at tne most desired location or time. In these instances suitable alternative media and locations may be chosen for the particular pathway in question and appropriate substitutions made within 30 days in the radiological environmental monitoring program. Pursuant to Technical Specification 6.14, submit as a part of or concurrent with the next Semiannual Radioactive Effluent Release Report a complete legible copy of the ODCM including a revised figure (s) and table for the ODCM reflecting the new location (s). t b , One or more instruments, such as a pressurized ion chamber, for measurin and integrating recording dosimeters. dose rate contineously ray be used in place of, or in addition t 60simeter (TLD For the purpose of this table, a thermoluminescent packet are cons)iderea as two or more dosimeters.is considered to be , as dosimeters for measuring direct radiation. Film badges shall not be used c Methodology for recovery of radiciodine shall be described in the ODCM. d Airborne particulate sample filters shall be analyzed for gross beta radioactivity daughter decay. 24 hours or more after sampling to allow for radon and thoron If gross beta activity in air particulate samples is greater ' than 10 times the yearly mean of control samples, gama isotopic analysis shall be performed on the individual samples. i
- Gamma isotopic analysis means the identif ka' tion and quantification of gamma-emitting facility. radionuclides that may be '.ttributable to the effluents from the I
The " upstream sample" shall be taken at a distance beyond significant- i beyond but of influence thethe near discharge. mixing zone. -The " downstream" samples shall be taken in an area ESR I Date ?<N Rev. I-56 t> 9 i _ .. _ , ..,_.v ----_ . ~ ~ . , , , . , , . . , -
r . _ s;Pg 3/412-8odca:74 Awo ' RADIOLOGICAL' ENVIRONMENTAL MONITORING = TABLE 13.4f1(Continued) i TA8LE NOTATIONS 9
A composite sample is one in which the quantity (aliquot) of liquid
. sampled is proportional to the quantity of_ flowing liquid and in which the L.P $
-method of sampling employed results in a specimen that is representative of the liquid flow. In this program composite s~ ample aliquots shall be collected at
. time intarvals that are very short (e.g., hoarly) relative'to the compositing; j period (e.g., monthly)inordertoassureobtainingarepresentativesample.,
h Groundwater samples shall be,taken when th4.; source is tapped for drinking
- irrigation purposes in areas where the hydraulic gradient or recharge- -
Properties are suitable for contamination.. , l I The dose shall be calculated for the maximum organ and age group, using the methodology and pare *eters in the 00CM Part II. 4 j p i nhI. _ _ , oathN Rev. 4 e e c h I-57 )
- - - - ~~ ~ ~ - ~ ~ ~ ' ' '
s;Pg 3/4 12-90dcn:74 - RWG TABLE 13.4-2 REPORTING LEVELS FOR RADI0 ACTIVITY CONCENTRATIONS IN ENVIRONMENTAL SAMPLES. o s Reporting Levels WATER
. ANALYSIS '(pci/L) AIRBORNEPARTICj) LATE(pci/kg,FISH: MILK . F000 PRODUCTS or GASES (pCi/m . wet) (pC1/L) (pC1/kg, wet)
Hi 20,000*
'Mn-54 ~1,000 30,000 Fe 400
.. 10,000' Co 1,000. 30,000- .
Co6) 300 10,000-In-65 300 . 20,000
. Zr-Nb-M 400**
-t-!3) 2 0.9 3 100 Cs-134 30 10 1,000 60 ,
1,000 Cs-137: 50 20 2,000 70 2,000
Ba-La-140 .. -
200** 300~
- For drinking water samples.
. of 30,000 pC1/L may be used. This is 40 CFR Part 141 value. -If no drinking water pathway exists, a value
** Total for parent and daughter.
e .,
.Date 3 o Rev. -:- .- I-58
. .. ._.._._m _ _ _ . . , __ . . _ . , _ . . _ _ . . _ _ _ _ _ , _ _ ,- . ..
- TABLE 13.4-3 _ .
.r-DITECTIONCAPABILITIESFORENVIRONMENTALSAMPLEANALYSISN) _
s
~
LOWER. LIMIT OF DETICTION (LLD)(b)(c) . WATER e AIRBORNEPARTICgLATE- ' FISH ~ MILK. ANALYSIS ' (pC1/L) or GASES (pC1/m ) F000 PRODUCTS: SEDIMENTS: +
.(pC1/kg, wet) (pC1/L)- - (pC1/kg, et) . (pC1/kg, dry) .
Gross Beta: 4: - 0.01 '.. H-3 4
'2000-4 :. - Mn 15 -
130. - Fe-59 30. 260 e -- 00-58,60 15 130 Zn-65 30 260 Zr-95 30 Nb-95 15: ,
~1-131~ 1(d)- 0.07; I 60
{ Cs-134 15 ~ 0.05 130 15 60: Cs-137 18 150 0.06 .150 18 Ba-140 80 - 180
-60 60 La-140.
f15 15 s Engr. 7 8 H. P. M Date 36/t'0 Rev. ~O ,
.a.
~
1-59
=
e'
~
..r pf u-noacm;is - gwy TABLE 13.4-3 (Continued 1 TABLE NOTATIONS (a)
This, list does not mean that only these nuclides are to be considered. Other peaks that are identifiable at 95% confidence level, together with those of the above nuclides. shall also be analyzed and reported in the Annual Radiological Environmental Operating report pursuant to Control 3.5. (b) Required detection capabilities for thermoluninescent dosimeters used ' for environmental measurements are given in Regulatory Guide.4.13. (c) The LLD is defined, for purpose of these Controls, as the smallest ' concentration of radioactive material in a sample that will yield a net count (above system background) that will be detected with 95% probability with only 5%
"real"probability signal. of f alsely concluding that a blank observation represents a For a particular measurement system (wi.ich may include radiochemical separation): ,
LLD = 4.66 sb E
- V
- 2.22
- Y ' exp(- AA ;) i where LLD is the "a priori" lower limit of detection as defined above (as picocuries per unit mass or volume),
sb is the standard deviation of the background counting rate or of the counting rate of a blank sample as appropriate (as counts per minute), E is the counting efficiency (as counts per disintegration), V is the sample size (in units of mass or volume), i 2.22 is the number of disintegrations per minute per picocurie. ' Y is the fractional radiochemical. yield (when ' applicable), X is the radioactive decay constant for the particular radionuclide, and 6t is the environmental samples is the elapsed time between sample collection (or end of the sample collection period) and time of counting. Typical values of E. V, Y and at should be used in the calculation. t Engr. N "6 H. P. F2 Nv' k 9 h4 e
6;rg4/4 At-itoccm:741,RWG ' 3,
=o - '
s. TABLE 13.4-3 (Continued)
--TABLE NOTATIONS- .
limit representing.the capability of:a measurement system an ; posteriori (after the fact) limit'for-a-particular measurement. Analyses shall be' performed routine in such a manner. that the stated LLDs will be achieved under , conditions. . 0ccasionally background fluctuations, unavoidably 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 i F Radiological Environmental Operating Report pursuant.to Control.3.5. -! (d) LLD for drinking water samples. n A i l L 4 4 Engr.
.H. P.
Date Rev. 1-61 , l l
LAND USE CENSUS CONTROLS 3.4.2 In accordance with LGS TS 6.8.4.f.2, a land use censu's shall be
conducted and shall identify within a distance of 8 km (5 miles) the location in t
i residence and the nearest garden
- of greater (500ft than 50 meachofth producing broad leaf vegetation.
APP'LICABILITY: At all times.
/
ACTION
- a. With a land use census identifying a location (s) which yields a calculation dose or dose comitment greater than the values currently being calcuhted in Control 3.3.4.1, identify the new location (s) in the next Semiannual Radioactive Effluent Release Report, pursuant to Control 3.6.
b. Withalandusecensusidentifyingalocation(s)thatyieldsa calculated dose or dose commitment (via the same exposure pathway) 20% greater than at a location from which samples are currently being obtained in accordance with Control 3.4.1, add the new location (s) to the radiological environmental monitoring program within 30 days. The s aGibs location (s), excluding the control station location, having the lowest calculated dose or dose comitment(s) pathway) may be deleted from this monitoring progr(am after October 31via of the year in which this land use census was conducted. Pursuant to Technical Specificatiot 6.14, submit as a part of or concur ent with , in the next Semiannual Radioactive Effluent Release Report a complete, legible copy of the entire ODCM including a revised fi table (s) for the 00CM reflecting the new location (s). gure(s) and SURVEILLANCE REQUIREMENTS l 3.4.2.1 The land use census shall be conducted duriog the growing season at i least once per 12 months using that information that will provide the best results, suchauthorities. agriculture as by a door-to-door survey, aerial survey, or by consulting local The results of the land use census shall be-included in 3.5.the Annual Radiological Environmental Operating Report pursuant to Control
- Broad leaf vegetation sampling of at least three different kinds of vegetation may be performed at the SITE BOUNDARY in each of two different i
direction sectors with the highest predicted D/Qs in lieu of the garden census. Controls for broad leaf vegetation sampling in Table 13.4-1 item 4.c. shall be followed, including analy:is of control samples. Engr. d d I-62 at fo
=,
~
.stPg3/4 12-14odemt74 RWG' RADIOLOGICAL ENVIRONMENTAL MONITORING INTERLABORATORY COMPARISON PROGRAM
-[
., CONTROLS 3.4.3 In accordance with- LGS TS 6.8.'4.f.3, analyses shall: be performed-on . >
r'adioactive materials supplied as part ofian Interlaboratory Comparison Program which has been approved by the Commission. APPLICABILITY: At all times. ACTION ' a; With analyses not being performed as required above, report the. corrective actions taken to prevent a recurrence to the Commission in
, the Annual Radiological Environmental: Operating Report pursuant- to Control 3.5.- -
SURVEILLANCE REQUIREMENTS i
;3.4.3.1-The interlaboratory Comparison Program shall be described in the ODCM A sunnary of the results obtained as part of the above required-Interlaboratory Comparison Program shall1be included: P the Annual Radiological Environmental Operating Report pursuant to Control :.
.s Engr.
.H. P. i
. Date- o Rev.
e f I-63 1 h9
- 8;Pg 6-16/odem:74 -'RW . !
e ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT
- 3.5 Routine Annual' Radiological Environmental Operating. Reports covering the operation of the unit during the pr.evious calendar year shall be submitted' prior to May 1 of each year.. The initial report shall-be submitted prior to May 1 of the' year following initial criticality.
The Annual Radiological Environmental Operating Reports shall include summaries, interpretations, and an analysis of-trends of the results - of the radiological environmental' surveillance activities for the report period, including.a comparison.(as appropriate), with. preoperational studies, operational controls and previous environmental surveillance reports and an assessment of the observed impacts of the plant operation on the environment. The reports shall ! also include the results of land use censuses required by Control 3.4.2. The Annual. Radiological ~ Environmental Operating Reports shall include the results of all radiological environmental samples and of all-environmental radiation measurements taken during the report. period i pursuant to the locations specified in the tables and figures in the OFFSITE DOSE CALCULATION MANUAL, as well as summarized and tabulated results of these analyses and measurements in the format of the table in the Radiological Branch Technical Position, Revision-1, Noven.be r 1979. In the event that some individual results are not available to 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'supplementar.y repert. The reports shall also include the-following: a sumniary description of the radiological environmental monitoring program; at least two legible maps.** l l A single submittal may be made for a multiple unit station.
**One map shall cover stations near the SITE BOUNDARY; a'second l
1 shall include the more distant stations. , I l- Engr. H..P. 45<<5 Date 7/iNo - Rev. X I-64 b%
. - --- _ _ , , _ - _ ~ . . . . . . ~ . - , , , ,
i ADMINISTRATIVE CONTROLS - - s;Pg 6-17/odem:74 - RWG 3.5- ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT (con covering all sampling locations keyed to a table giving distances and directions from the centerline of the reactor-plant; the results of licensee participation in the Interlaboratory Comparison Program, required by Control 3.4.3 discussion of all deviations from the Sampling Schedule of Table 13.4-3; and discussion of all analyses in which the LLD required by Table 13.4-3 was not achievable. 3.6s SEM1 ANNUAL RADIOACTIVE EFFLUENT RELEASE REPORT
- Routine Semiannual Radioactive Effluent Release Reports covering the operation of the unit during the previous 6 months of operation shall be submitted within 60 days af ter January 1 and July 1 of each year. The period of the first report shall-begin with the date of initial criticality. i The Semiannual Radioactive Effluent Release Reports shall include a summary of the quantities of radioactive liquid and gaseous effluents and solid waste released from the facility 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 format of 1. June 1974, Appendix with data summarized on a quarterly basis following the B thereof. , The Semiannual Radioactive Effluent Release Report to be submitted 60 days after January 1 of each year shall include an annual suimnary of hourly meteorologial 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 and atmospheric stability, and precipitation (if measured), or in-the form of joint frequency distributions of wind speed, wind direction, atmospheric stability.** This same report shall include an assessment of the radiation doses due to the the previousliquid radioactive andyear. calendar gaseous effluents released from the unit or station during This same report shall also include an assessment of the radiation doses from radioactive liquid and gaseous effluents to MEMBERS OF THE PUBLIC due to their activities inside the SITE BOUNDARY (Figures 12.2-la and 12.2-lb) during the report period. All assumptions used in making these assessments (i.e., specific activity, exposure time and location) shall be-included in these reports. The assessment of radigtion doses shall be performed in accordance with the methodology and parameters of the OFFSITE DOSE CALCULATION MANUAL (ODCM). l i
*A single submittal may be made for a multiple unit station.- The submittal should combine those sections that are common to all units at the station. **In lieu of submis'sion with the first half year Semiannual Radioactive Effluent -
Release Report, the licensee has the option of retaining this summary of required meteorological request. data on site in a file that shall be provided to the NRC u on Engr. H. P. I-65 Date Rev.
ADMINISTRATIVE CONTROLS s;Pg 6-18/oticmh74 - RWG f 3.6 SEMIANNUAL RADIOACTIVE EFFLUENT RELEASE REPORT (Continued)
~
The Semiannual Radioactive Effluent Release Report to be submitted 60 days after January 1 of each year shall also include an assessment of radiation doses to the likely most exposed MEMBER OF THE PUBLIC from reactor releases and other nearby ; uranium fuel cycle sources (including doses from primary effluent pathways and direct radiation) for the previous calendar year to show conformance with 40 CFR Part 160, Environmenta,1 Radiation Protection Standards for Nuclear Power Operation. Acceptable methods for calculating the dose contribution from liquid and' gaseous effluents are given in Regulatory Guide 1.109, Rev. 1,.0ctober )977.~ The Semiannual Radioactive Effluent Release Reports shall include the following i information for each type of solid waste (as defined in 10 CFR Part 61) shipped offsite during the report period: i
- a. Container volume,
- b. Total curie quantity (specify whether determined by measurement or estimate),
- c. Principal radionuclides (specify whether determined by measurement or l
estimate), i d. Source of waste and processing employed (e.g., dewatered spent resin, ; compacted dry waste, evaporator bottoms), e. Type of container (e.g., LSA, Type A. Type B Large Quantity), and f. SOLIDIFICATIONagentorabsorbent(e.g., cement;ureaformaldehyde). The Semiannual Radioactive Effluent iiele::e Repom shall include a list and description of unplanned releases from the sitt to UNRESTRICTED AREAS of radioactive materials in gaseous and liquid effluents made during the reporting period. The Semiannual Radioactive Effluent Release Reports shall include any changes made during the reporting period to the PROCESS CONTROL PROGRAM (PCP) and to the 00CM, as well as a listing of new locations for dose calculations and/or environmental monitoring identified by the land use census pursu' ant to Control 3.4.2. 1 The Semiannual Rdioactive Effluent Release Reports shall also include the following: an explanation as to why the inoperability of liquid or gaseous effluent monitoring instrumentation was not corrected within the time specified in Controls 3.2.1 or 3.3.1, respectively; and description of the events leading to liquid holdup tanks or gas st,orage tanks exceeding the Control limits.
~
Engr.dh_ H. P. /6 Date M/W Rev. __8 I-66 n
ADMINISTRATIVE CONTROLS - stPg-6-23/odem:74 - RW
'3.7 MAJOR CHANGES TO RADIOACTIVE WASTE TREATMENT SYSTEMS (Continued)'
1 Licensee-initiated major changes to the radioactive waste systems (liquid, l l1 s gaseous, and solid): i
- a. Shall be reported to the Commission..in the Semiannual Radioactive i Effluent Release Report for the period in which the change was made effective. The discussion of each change shall'contain' '. ~
l
- 1. A summary of the evaluation that led to the determination that the change could be made in accordance with 10 CFR 50.59; 1
- 2. Sufficient detailed information to totally support the reason for the change without benefit of additional or supplemental information; 3.- A detailed description of the equipment, components, and processes involved and the interfaces with.other, plant systems;
- 4. An evaluation of the change which shows the predicted releases of radioactive materials in liquid and gasesous effluents and/or quantity of solid waste that differ from those previously predicted in the license-application and amendments thereto;
- 5. - An evaluation of the' change which shows the expected maxhnum exposures to individual in the UNRESTRICTED AREA and to the general population that differ from those previously estimated in the license application and amendments thereto;
- 6. A comparison of the predicted releases of radioactive materials,-in liquid and gaseous effluents and in: solid waste. to the actual' releases for the period prior to when the. changes are to be made; 7.
~
An estimate of the exposure to plant operating personnel.as a result of the change; and j 8. Documentation of the fact that the change was reviewed and found acceptable by the PORC. '! l
- b. Shall be reviewed and accepted by the PORC prior to implementation.
l l j ES;: 9ds l Date Y/,40 i Rev. M I-67 1 1 m,
44d,d- e .J-.. ..'s.' E 4a m ..m m--e- - - ,,
) i i
9 6 A , 1 f
.l l 1
.*.. '1 1 1 e s
- j 4
1 t I'
. 1 PART II a
l I l i l l t O
- t s
W I bS m.. _ _ ___m- _ _ .___-___m_____ _____m-m e _m-a t----*-. , .- .,&--eew+ ew-a -.r- .m h-w~ + *y v
l 1.0 Liquid Efiluents '
1.1 Radiation Monitoring instrumentation and Controls The liquid ernuent monitoring instrumentation and' controls at timerick for controlling and monitoring normal radioactive material releases in accordance with the Limerick Technical y Specifications tre summarized as _follows: ,
- 1) Liquid Radwaste System: The liquid radwaste dischary monitor (RISH63-0K604) . provides 'an alarm and automatic termination of radioactive material releases from the liquid radwaste system as required:
by. Technical Specification 6.8.4.d.1. Additional design features of the liquid radweste' system which prevent inadvertant releases to th0 environment in = clude 1) redundant discharp valves, 2) single dis-charge line with loop seal and siphon breaker to - eliminate' probability of inadvertent discharges,
- 3) Low Cooling Tower Blowdown flow interlock which .
' isolates the radweste discharge line.
- 2) Service Water System: - The Service Water discharge -
monitor (RISH10-lK605 and RISH10-2K605) provides an alarm upon indication of activity in the service water system - as required by Technical Specification 6.8.4.d.l. While the service water system is not a normal release pathway,- the monitor provides an indication of potential problems due to excessive leakage of the heat exchangers. In ad-dition, the service water side of the fuel pool. heat ex-changers is kept at a higher- pressure than the 'shell side : to prevent potential' radioactive contamination of the service water. .
- 3) RHR Service Water Svstem: The RHR Service' Water '
Radiation (RIIRSW) Monitors (RISH12-0K619A, RISH12-OK619B,'.RISH12-lK619C, RISHlklK619D RISH12-2K619C, and RISH12-2K619D) provide alarm and automatic termina-tion of radioactive material release from the RHRSW - system,las required by Technical Specification 6.8.4.d.l. While the:RHRSW system is not a normal ^ release pathway, the monitors provide indication of potential problems due to excessive leakage of the heat exchanprs. 1.2 Liquid Effluent hionitor Setpoint Determination-Per the requirements of Technical Specification 6.8.4.d.l - I alarm setpoints shall be established for -the liquid effluent - . monitoring instrumentation to ensure that the release con-centration limits of Specification 6.8.4.d.2 and 6.8.4.d.3 g Eny H. P. Date Rev. = 1
4 * ' j are met (i.e., the concentration of radioactive material 1, I
~.eleased in liquid effluents.to UNRESTRICTED ' AREAS shall be limited to the concentrations specified'in 10 CFR 20, Appen- i dix B, Table II, Column 2, for. radionuclides and 2 OE-04 4
- pCl/ml for dissolved or entrained noble gases).
' 1.2.1 Radwaste Discharse Monitor' and Discharse Flow Rate - -
RISH63-0K604 -- W setpoint for the liquid radwaste discharp monitor . i i and flow rate at LGS are determined by the following i
; equations.: The radwaste discharp monitor high-high :
alarm / isolation setpoint is calculated at least monthly . . , based on isotopes detected in the liquid radwaste sample 4 tanks released during the previous month or on any ' specific sample tank being released (EC,..), i i the required rrdnimum cooling tower blowdown flow at time ,
. of discharp (CTBD), and aversy liquid radwaste dis-charp flow (RR). The flow rate determination is calcu-lated for each release and the MPC fraction calculated includes, in 'the concentration mix,' the most recent results from 1), the quarterly composite for Sr-89, Sr .
90, and Fe-55, and 2) the monthly composite for H-3, and
- 3) the sample (s) for dissolved and entrained noble pses.
, If the calculated setpoint is'less than the existing '
setpoint, the setpoint will be reduced to the new value. If the calculated setpoint is greater than the existing setpoint - the setpot. may remain at the lower value or-increased to the cak. ated value. If there were no sample tanks released or no activity '
. detected during the previous month, then the calculation is performed using release' data from the most recent month'during which isotopes were dgtected.' In addition. '
l if there were no sample tanks released during the pre-vious month,' chemistry supervision may substitute more restrictive values (e.g., tritium) based on the plant - sampling data. Engr _ H.P. Date - Rev. _ 1 em 9 ,
-. , ,v.,-- . - - , . . . - -
3 } h w - 1.2.1.1 Setpoint Determination - RISH63-0K604 The setpoht for the liquid radwaste discharge . t
.. monitor is determined by the following equation:-
3 CPM @u) 8- - I"(S)(RR)[E(C,)/MFC,)] i i ~ (DC%)(RR+CTBD) * (RR+CTBD) . .
, (S)(E)(RR)[E(C% ,/MPCw.)] , @RD) ( I"O $
i t k where: " r, CPM @u) = . Calculated liquid redweste dis- , charge monitor.(RISH63-OK604) count: c rate. attributable.to the pmma emit-ting radionuclides, cpm,( EC%,- = the sum of tho' concentration - of the identified pmma emitting
, nuclides (/Cl/ml), , CTBD- = the required . minimum: cooling tower.
- blowdown rate at: time of dischary, . <
1 RR0 = averase liquid:radweste_ dischary --' flow '( spm) . . BKG@an) = background count' rate of liqui.d. radweste discharge monitor (CPM), E = the gross perna detection ~ efficiency of the Liquid; radweste discharge. 1 monitor (Ki/s.1/ cpm), and--- - l l H.P. 6 Date SA/90 Rev._f_ _.
-( ;- .
1 S = 5; margin of safety factor to assure ! that the release is terminated prior to 10 CFR 20 limits being exceeded. > 4
-Included in this factor are errors i associated with monitor uncertainty, '
. sampl!ng uncertainty, flow rate un- '
t certainty, and the contribution of ,, S. other release paths (Service Water, and RHRSW), which are not no.mally. contaminated. E(Cg ../MPC,,,,,) = the effec- - 3 l tive samma MPC ratio for the mixture of . radionuclides-in the !1q.
.uld radwaste discharge
, line (unitiess) where:
C. g = the concentration of each - . l_ j identified samma emitting radio-nuclide i in the liquid effluent (un - diluted) (pCl/ml) MPCs,,,,, = the MPC value corresponding to radionuclide i from 10 CFR 20 Appen-l dix B, Table II, Column 2 (dis- . solved and entrained noble gases MPC '
= 2,0x10'i p ci/ml) (pCi/ml).-.
E(Cig/MPCg) = the effective nongamma MPC ration for the mix- g ture of radionuclides in the lig-uid radwaste discharge line - (unitiess) where: Cg = the concentra'tlon of each identified nongamma radionuclide 1 l in the liquid effluent (undiluted) (PCl/ml). - MPC, = the MPC value correspond-
, ing to radionuclide'l from 10 CFR l 1
-20: Appendix B Table II, Column 2 (dissolved and entrained noble-gases MPC = 2,0 x 10
#Cl/ml) (pCi/ml)
Engr H. P. - Date '
, Rev.
4
a a q lN
'.NOTE: .The concentration mix must include the most recent sample data for H-3, St-89, St-90, Fe- i t
. . 55, and dissolwd and entrained noble gases. . t
' ).2.1.2 Flow Rate Determination e
. NOTE: LF. the 'offectiw MPC ratio for the mixture of
- radionuclides. [E(Ci /MPCg))
is 51.0,'- M a flow rate setpoint determination is not re- i quired. A@ there is no' limit'on discharge flow - i rate. , jfF. a flow rate determination is required,'
~
M the 'setpoint for' the liquid radwaste flow rate is determined for each release by the following- r
' equation: .
FLOW ggg) 5 (SF)[4C I I' ) g)-1] where: - FLOWp = flow limit for radwaste discharge line (spm) CTBD = required minimum cooling tower blowdown flow for time of release SF = Sh margin of safety factor to assure that the -. release does. not exceed- 10 CFR 20 limits '
- t. i E(Ci /MPC) i = the effective MPC ratio for the' mix- ' l ture 'of radionuclides in the liquid rad-waste discharge line (unitiess) l C = the conuntration of each identified
' radionuclide 1.in the liquid effluent (un-diluted) (Kl/ml). t IB ' H.P. Date ' l Rev. l. I s bS
.'1
- ,w - ,. . ~ .. . . . . . . , _ . - - - . . .
. , . . - , , . . . - . . < ..,e-~,.-. , . ,. .- .
n.< .. j h
' MPC3 = the MPC value corresponding to '
.radionuclide i from 10 CFR. 20 Ap-pendix B; Table II, Col; 2, (dis-solved and entrained.. noble gases .
, (MPC = 2.0x10$Ci/ml)
(#Ci/ml) ~ ,
) . . *
. . NOTE The concentration mix must include the <
l most recent sample data for H-3, Sr-89,- Sr-90, Fe-55, and dissolved and entrained - noble gases.- . 1.2.2 Service Water Radiation Monitor. - RISH10.lK605,-2K605 1 The Service Water Monitor high-high setpoint is determined by the following equation. . The monitor. high- t t high' alarm setpoint is calculated monthly based on the . background count rate ~ If the' calculated setpoint is l ; less than the existing monitor setpoint, the setpoint l will- be reduced to the new value. If the calculated . setpoint is greater than the existing setpoint, the' set-point may remain at the existing setpoint or increased
~
-to the. new value, iTo assure that a high background i count rate does not prevent adequate monitor sensitivity to meet the requirements of technical specifications 6.8.4.d.2 and 6.8.4.d.3, a maximumSonckground count rate l
1 of 300 CPM shall be used for the alarm setpoint - determination. 1.2.2.1' . Setpoint Determination The setpoint for the Service Water Monitor is determined by the following equation: - H.P. Date o Rev. - b3 P
- - - + .- - e - .- . . , _
-- ~
3_______-____------------+------ . r.; - CPM,, s Z,# CRB,w) - (1-3) . ' where: ' CPM,, a Calculated Service Water Radiation - Monitor (RISH10-lK605,-2K605) count 3 rate, CPM ' l _ Z,, = 3, multiplier to establish < monitor setpoint count rate above back - j ground count rate (unitiess)- CRB,, a Service water monitor (RISH10-!K605
-2K605): count rate attributable to back .
ground radiation; CPM. l.2.3 RHR Service Water Monitor - RISH12-OK619A.-OK619B,
-IK619C -IK619D --2K619C,-2K619D -
The RHR Service Water Monitor high-high setpoint is determined by the following equation. The monitor high-
-high alarm / isolation setpoint is calculated monthly. I based on the background count rate. . If,the calculated f
setpoint is less than _the existing monitor setpoint,- the setpoint will be reduced to the new value. 41f the j calculated setooint is greater than the existing set-', point, the setpoint may' remain at the existing setpoint . or increased to the new value. To $sure'that a high -. '
' background count rate does not prevent adequate ' monitor.
sensitivity to meet the requirements of technical speel-fications 6.8.4.d.2 and 6.8.4.d.3, a maximum background count rate of 300 CPM shall be used for the alarm set-point determination.
- Date c' ;
- Re'v. '
. . _ .. _ _ . . . ._._ _ _ _ ._ _ . _ _ . _ _ _ . . _ ~ .__ _ _.
,, .l
- i
}
l 1.2.3.1 Setpoint Determination ~ I
.l The setpoint for the RHR Service Water monitor is determined by the following equation:'
CPMagas,s Zagas,(CRBRHasw) (l-4). .i
~
)
, wherel ' -
, ;j
-CPMRHR8W = Calculated RHR~ Service -
' Water Radiation Monitor ~
( RISH12-0K619A,-0K619B, . j
-lK619C,-lK619D,-2K619C,
--2K619D) count rate, CPM :
ZRHasw. = 3, multiplier tJ estab-lish monitor setpoint count rate above the background -
' count rate (unitiess)-
'\
CRBRHR8W = .RHR Service Water' Radisk tion ~ Monitor'- .i (RISH12-0K619A,-0K619B.
-lK619C.-lK619D,-2K619C,
-2K619D) count rate attributable to background '
radiation, CPM 1.3 Liquid Effluent Dose Calculation' - 10 CFR 50 ~ 1.3.1 Members of the Public Dose - Technical Specification ODCM 13.2.3 limits' the dose or-l dose commitment to MEMBERS OF JHE PUBLIC from.radioac-tive materials in liquid effluents from Limerick Geners-- ting Station to:
- during any calendar quarter:
' $3 mrem to total body
$10 mrem to any organ l-
- during any calendar = year:
EngrM l H.P. j Date l' . a Rev. Y ~
.s.
b%
_ , ;.7 _, . f , . .. n s6_ mrem toLtotal body ' - i
., 520 mrem to total organ' +
l I l l . 3 Per Surveillance Requirement 'ODCM 13.2.3.1 the cumula-
/'
tive dose contribution from liquid: effluents for the
,l current calendar quarter and calendar year shall-be determined at least once per 31 days 'in' accordance with
~
l the following calculational methods. These equations are for the three aquatic environment exposure pathways -- i
'(potable water, fish, shoreUae exposure) in the -
Limerick aquatic environ aent._- Only real pathways are I addressed for each receptor. The receptors and associa-ted pathways are listA below. Doses from each real i pathway are summed to give dose at the receptor. -The . l ' monthly results are accumulated to give the quarterly.- doses and the quarterly results are accumulated to give the annual doses. l l Receptor Dist. %thieys l Location . ( mi)-- Potab'e Water Fish . Shoreline
~
l ' 1 : s LGS Outfal! 0- x x Citizen's Utility. 2.5 xi x -- x-x- Phoenixville Water -' Phil. - Sub.' ' Water .
- 9. 0 - x, x 4 13.6 x .x i Crew- Course 37.8 x t En H.P.
. Date j Rev.- 1 v j en s .
.~ . . _ _ _. .. - __ _
3 l 3 ..
, , g . -- . -
, ti t
~
1.3.1.1 Potable ' Water Pathway;. . U Rm ' = 1100 Q,Dg ,) exp(-h(12)) . ' (1 5)
.g. -
r.. E
'l.3.1.2' Fish ( Aquatic' Food)- Pathway i
U' - I
, Rm = 1100 {Q;B3,Dg ,) exp(-h (24)) - ( l-6)
.a 1.3.1.3 Shoreline Deposition Pathway '
' Rm = 110,000
'U,W
. Q;Ti Dun exp(-ht,) [1-exp(-h(1.752E+5))) (1-7)'-
where: i B;, - equilibrium bioaccumulation factor for nuclide i in ! pathwsy p, expressed as the ratio of the concentration in' .l biota, in pCi/ks, to the radionuclide concentration in '
- water, in pCi/ liter (liters /kg)'
l . . l: 1 L : e h b H. P. Date y i. Rev. y 10 - ~
*\
,e 9 f
a; , 4
'I -
b \
. ELEMENT FISH - ELEMENT FIS'H H' 9.0E-Ol- -NB- 3.0E 04 L C 4.6E 03 MO 1.0E 01:
NA . 1.0E'02 TC 1.5E 01 P' 3.0E 03 RU. - 1.0E 01'
~ !1 CR - 2.0E 02 RH!
MN 4.0E 02 TE 1.0E . 01 -
' 4.0E 02:
] 1 1
FE- 1.0E 02: ~!. 1.5E 01 I CO- 5.0E .: 01 CS- 2.0E 03 ' NI . 11.0E 02 =BA 4.0E 00 r CU. 5.0E 01 LA. . 2.5E 01 -1 . ZN 2.0E 03l 'CE. : 1.0E 00 -' .! BR 4.2E 02 PR 2.5E 01 .b RB 2.CE 03 ND- 2.5E 01 t SR 3. 0E . 01 ' 'W. 1.2E 03 . Y - 2.5E 01 P 1.0E 01 ZR . 3.3E 00 Ref: 1) Regulatory ' Guide 1.109, Rey. I, Table A-1
' 2) Letter LTR 881209L001,'_ from R.i J,- Clark, U.S.N.R.C., to G. 'A. Hunger, Philadelphia Eleccic Co.', December 9,.1988, transmitting evaluation of Limerick ODCM. - '
t 4
. t H.P. . % S ;
v
'I i
1 l
=,
?
i
F
. . . , . n
?
Dg,; = dose factor specific to'a given ap group' -
' '- s, radionuclide 1, pathway p, and organ j which +
' can be' used to. calculate radiation dose ( 1) ' from
* - an intake of a radionuclide, in mrem /pCl, or. (2) . .
from exposure to a given concentration of a s radionuclide in sediment, in mrem /hr' per ' . .)
. -t 2 ~
pCi/m .'. Values are listed by age group in ^
~ Table 1-1. 7 F -= waste dilution Ow trwo of liquid effluent dilu-8 tion flow / number of batches (ft /sec). -
M,
~
=
' dildtion factor at point of exposure or,at
. point' of withdrawal of drinking water (dimension-
-less) : ' Values are graphically listed by receptor ~
location in Figures: 1.3.1-1 -to.1.3.1-5. Value will be based on average monthly river flow.1
. Q, . = total release. of nuclide. 'i' for time period (Ci). t R ,; = ' total dose for' calculation time period to organ j of individuals of age group.a from all .
nuclides i in pathway b (mrem) Ti = radioactive half-life of nuclide i (days) U., . = usage factor specifying exposure time or ~ intake rate for an individual of age group a as-sociated with pathway p (hr/yr,: liters /yr, or kg/yr) ' I 3 i r Engr - H. P. Date [
- Rev. -
O
^ h1
---__'...____.. . i,_. . - - . .,.._ . . . . , . - _ . - . . . , , a ., ,,, . , , , , . , ,,..,...n, ,..,,..w... , .,
.- .. ~. __ _ -. .
e> , .
*[
.: 1 l
s > l Pathway LInfant: Child TeenL i Adult ' i Fish - - - 6 . 9 11 6' ; 21' Potable 1W a t.e r ; i ( 1/yr) - 330* 510' 510' 5 730*
. Shoreli ne '
Recreation ( hr/yr) -- 14* 67* 12' Shoreline Recreation (hr/yr) -- 90b : 6006 '600b Ref: -.' Regulatory Guide 1.l(9, Rev.1. Table E-5
-b
, EROL Table 5.25-3 1
?
W = shoreline width factor (dimensionless) =. 0.2. 1 Ref: Regulatory Guide 1.109. Rev. ~1
. l.752E+5 L =' time period 'during which sediment is exposed i
to contaminated water-(hrs) (midpoint. of plant life = 20 yrs) - h = radioactive decay constant of nuclide 'i' (hrl)- 12 = delay time for. potable water pathway in hours to - allow for nuclide decay during transport through'. the water purification plant. and the water dis-tribution system. Ref: . Regulatory Guide 1.109, . . Rev. 1, App. ~ A _ 24 - delay time la hours for fish pathway to allow for nuclide decay during transit through the food- : chain, as well as during food preparation. .Ref: Regulatory Guide 1.109, Rev.1,' App. A 1100 = factor to convert from Ci/yr per. ft*/sec to pCi/ liter . 110,000 = factor to convert from.Ci/yr per ft*/sec
. to'pCi/ liter and to account for proportionately constant (100) used in sediment radioactivity .l model.
O i l
. R##
l ' [ .. l l l
e 1 3
. i 1.4' Liquid Effluent Dose Projections -
s ODCM 13.2.4' requires that the liguld radwaste treatment ' system shall be operable and appropriate portions of the
-i systems s' hall be used to reduce the radioactive materials in. I liquid waste prior to their discharge'when the projected ~ ~
L L doses due to the liquid effluent to UNRESTRICTED AREAS would exceed: i
- 0.06 mrem /31 days to the _ total body-or 0.". mrem /31 days to any orrin
' The applicable liquid radwaste treatment processing equipment for maintaining radioactive material releases ALARA are delineated in Figure 1.4-6. i L
I Dose projections are made at least once per 31-days by the 1 following equationt:- i Dib, = ( D,6/d) = 31 days - ( l-8) D, , = (D, /d) = 31 days ( l-9) - 1 ' where: ' Dibp = the total body dose projection for the cur-rent 31-day period (mrem) Dib = the total body dose to date for the current calgndar quarter as determined by-equation- 1-5, l-6, and l-7 (mrem) ' D , = the maximum organ dose projection for the- . current 31-day. period (mrem) i H st; naa Rev. # '
.o
- -- . v - , ~< . . . ~ . - - . , . . - - - - - . . , . . . - . - - - - , - . - . - . . . - , - - - . ~ . . . - . . - - - - -
- o. > .
.i I
1 D ., = the maximum ' organ dose to date for the'
~
' current calendar quarter as determined by equa.
tions 1-5,1-6, and 1-7 (mrem) i d = the number of days in the current- calendar v quarter at the end of the release (days).. The minimum time elapsed is seven (7) days. ' ' ' ' 31 days - the number of days of concern ( 2.0 Gaseous Effluents A 1 2.1 Radiation Monitoring Instrumentation and Controls 7,
, he. gaseous effluent monitoring instrumentation and controls i; at Limerick for! controlling and monitoring radioactive .,
u material releases in accordance with the~ Limerick Technical Specifications are summarized as follows:
- 1) North Vent (Common): The plant gaseous discharses via this vent are monitored by two Particulate, Iodine '
and Gas (PIG) monitors (RY26-075A and RY26-075B) in-parallel and by the Wide Range- Accident Monitor:(WRAM) , V
\
(RIX26-076); The PIGS have separate Particulate, Iodine,' . [ and gas sampling and monitoring channels but the Station 3 c Technical Specifications require only particulate and M
-iodine sampling and noble. gas monitoring.' The WRAM has extended range (via three channels) noble gas monitoring and particulate and lodine' sampling capability. In addi-1 tion, the WRAM provides an isolation of the large Drywell
. Purge and Vent valves. .
Il . Engr
-)
H. P. -
, Date Rev. M
-]
1 l 1
)t -
o . a
- 2) South Vent (one per unit):; The plant gaseous; dis- i s- !
charges via each South Vent are monitored by two redundant =' PIG monitors (RY26-185A,B and RY26-285A,B). As is the case of the North Vent, each PIG has separate particulate,
- iodine, and gas sampling and n'onitoring channels buIthe -
Station ODCM I requires only particulate and , lodine sam ll pling with noble ~ gas monitoring. 4 I'
- 3) Hot Maintenance Shop (Common): Due to the composition: of ,
l
' the radioactive materials :in the effluent stream (i.e.,
j very low potential for noble gases), this release point is sampled by a Particulate and Iodine (P&I) Monitor (RY26 ' 025). The P&l monitor has separate particulate and iodine sampling and monitoring channels but the Station ODCM I re-l quires only particulate and lodine sampling.- r 2,2 Gaseous Effluent Monitor Setpoint Determination ODCM 13.3.7.3 requires. that alarm 'setpoint 'be established - l for the noble gas effluent monitoring channels (RY26-075A,B; RY26-185A,B; RY26-2tSA,B; and RIX26-076) to ensure that. the release rate of radioactive materials does not exceed the , limits of ODCM 13.3.2.a, which correponds to a dose rate at l the, SITE BOUNDARY of 500 mrem /yr to the total body or.3000 mrem /yr to the skin.- This specification also states that l EngrM. a.P. /u
- Rev
~
b% l
_ . . _ .- - _ . . . . . - -. - - _ _ . - - . . _ - . . - . . . . - . _ - . .~
. I
, a i
the dos rates from 1+13), 1-133, tritrM i, and all a 4 radionuclides in particuke form Oh half-lives greater ! than eight days, shall be limitk to a maximum of 1500
, miem/yr to any organ (Inhalatio.t pathway only).
i ODCM I 11: nits are expressed th terms of dose rate, while the lastraments 'vhich monitor effluents produos data in units of f
- concentration of radioactivity (i.e., PCl/oc). Itis s
therefore necessary to calculate the correspondl g con. centration of effiuent release.which will result in the dose rate limit being reached at the site boundary. This cal- ! culation is made more complex by the use of multiple release , points at 1.GS. ' Qalculational Bases The alarm retpol'nt calculation is performed monthly and is based on analytical results of grab samples'from the ap-propriate relene point. The relative concentration of each. Identified radionuclide fu the grab samp'es is determined . . and the data are used to perform a setpoint calemmilon for that aucude mix and release point. i 4 i S ! onte Rev.,/,_ drid
. 17 - ;
I t> 9
)
. . . _ . -_ _ . ~ . . _ . _ . . . . . _ . . _ . . _ _ . . _ _ _ . , _ _ , . _ -. _ . . . .
e I l
. The highest calculated annual average relative concentration I
(X/Q) for an area at or beyond the site boandary (1.lE-05 sec/Ms; NE sector) is conservatively used in the setpoint 1 I ! g calculation. , I i Maximum flow rates through the North and South vents, are used in alarm setpoint calculations. This is the most con- < servative situation and is necessary since flow can vary. By using maximum values, any flow less than the maximum r<ill assure that the monitor wl!! alarm before release rate limiu are exceeded. For each release point the following concentration is determined: a) the noble gas release concentration which ' would cause a SITE BOUNDARY total body dote rate of 500 [ mrem /p and a skin dose rate of 3000 mrem /yr. The fractional contribution of noble gas is calculated for ea h release point. The fractional contribution to the whole body and skin dose rates due to noble gases is calcu. lated by taking the product of this fraction and the' limit-ing concentration. A comparison of this concentration for i whole body and skin dose rates due to noble gase releases is i made to determine if the whole body or skin dose limit will be most restrictive. It is expected that the whole body Engr H. P. Date # ~ hv. p i, tm 9 I-
. . - . . , . , - . - - . . . . - _ - - , , . - - . ~ . . . - - - .- - . .. ,
o
. 1 l
limit will always be most restrictive, but the comparison is - i s necessary to assure compliance with ODCM 1. The sum of' the ' l~ contributions from each release point, independently calcu-l1 i
, lated for lodines and noble gases, will equal the maa.imum I instantaneous release rate allowed from the site.
l l The purpose of calculating the release rate which cor-responds to the site boundary dose limit is 391 to determine an acceptable release rate, but to determine the maximum release rate which may not be exceeded. It is agt intended that releases will be maintained at or i near thl: 11mit, and in fact, requirements to maintain i offsite doses As Low As Resonably Achievable ( ALARA) are
. specified in ODCM 13.3.3 and ODCM-13.3.4.
l 2.2.1 North Vent Noble Oss Effluent Monitors - RY26-075A-3, RY26-075B-3, and RIX26-076-2 Th< North Vent Noble Gas' Effluent monitor high-high setpoint is calculated monthly baso(on the grab sample results performed in accordance with ODCM 13.3-3. Due l to the incorporation of the ALARA philosophy in the design and operation of the 1imerick effluent systems,
, release polht grab samples may not identify any .
b ef i H. P. ' Date Rev.- 19 i W9 w
radionuclides. With this situation, plant staff may, i s use the results of the last grab sample which identified radionuclides or use the 6 uit setpoint s which h based on expected concentration ratios as i reported in the FSAR. If any calculated alarm setpoint is less than the existing monitor setpoint, the set- ' point will be reduced to the new value. If the calcu-lated setpoint value is greater than the existing value, the setpoint may remain at the lower va!::e or ' e lacreased to the new value. 2.2.1.1. Setpoint Determination The setpoint for the North Yent Noble Gas Ef-fluent Monitor is set at or below the lesser of ' the NVSPyaws or NYSPgag value. The l Alert setpoint is not to exceed 1.1 E-04 i ; Kl/cc, per LOS FSAR Table 11.5-2, using the two-unit maximum North Yent flow rate. I (VFyywo)l500){DCml NVSPnowa5 (3,w5 E+W)qt Cw)(IU)) (2-1)
. (VFyvwoll3000)[DCwl NV5PNom 8 '
K5 E+W)R(Cw)(Lp1.1%)} (2-2) where: ,
.i e
Engr H. P.
' Date Rev.
20 -
- J i
NYSPga,, = North Yent setpoint - Noble Gas Whole Body (#Cl/cc) NYSP3agg - North Vent Setpoint - Noble Gas Skin (#C1/cc) VF wna
' = Fractional contribution to site . t boundary noble ans dose rate front,the North Vent a calculated in equation f l 2-7. (unitiess).
$00 = Total body dose rate limit (mrem /yr) !
e 3000 = Skin dose rate limit (mrem /yr) i T4 m = Total noble gas activity from North Vent grab sample (#Cl/cc) li , 3.4475 E+09 = Conversion factor s
= (l.IE-05 sec/m )(10' pCl/#Cl)(664,000 cfm)(h min /sec)(2,832E+04 cc/ft') (2-3) l where:
s 1.lE-05 sec/m = highest annual average relative concentration (NE lt' Sector). 109 pCi/ mci = units conversion ' 664,000 cfm = maalmum North Vent flow rate for (wo unit operation kmin/sec = uniti conversion 2.832E+04 cc/ft" = units conversion ' Cm = concentration of noble gas-
. nuclide i as determit ed by radionnalysis of Norti Vent grab i sample (PCl/cc)-
K, = Total body dose consorsion factor , for noble gas nuclide n (mrom/yr por . 1 pCl/ms , from Table 2-1) Eny H. P. Date Rev. 21 - < 1
=, l l
i I i Ij
- Beta skin dose conversion' factor ' for noble gas nuclide 1 (mrem /yr per pCl/m' , from Table 2-1).
i M, = Gamma air dose conversion factor l 3 for noble gas nuclide.1 (mrad /yr per ' pCl/m8 . per Table 2-3). ~ I I 2.2.2 South Vent Noble Gas Effluent Monitors - RY26' 185A-3, - s RY26-185B-3.' RY26-285A-3. and ' RY26-2858-3 l Each unit's South Vent Noble Gas Effluent monitor hlsh- ; high setpoint is calculated monthly based on the grab i sample results performed in accordance with ODCM 13.3-3. Due to the incorporation of the ALARA philosophy in the de:Ign and operation of the Limerick effluent systems, ' release point grab samples may not identify any radionuclides. With this situation, plant staff may use the results of the last grab sample which
- t identified radionuclides or use the default setpoint "
i which is based on expected concentration ratios as-reported in the FSAR. If any calculated alarm setpoint is less than the existing monitor setpoint, the set-point will be reduced to the new value. If the calcu-lated setpoint value is greater than the existing ' value, the setpolut may remain at the lower value, or lacreased to the new value. 4 i Engr H. P. 1 Date l
. Rev.
We % l
-, _ , _ _ . . _ _ . _ _ _ , _ _ __._____________________I
l
- I i
A 2.1.2.1 Setpoint Determination The setpoint for the South Vent Noble Gas Ef-1 - fluent Monitor is set at the lesser of the i SYSPNows or SYSP3ag value. SYSPyg,, and SYSPNos are calculated for each unit's South Vent. The Alert setpoint is not to exceed 3.4 E-06 Kl/cc, per LGS FSAR i i Table 11.5-2, for each unit's South Vent Noble I Gas channel, using each unit's maalmum South Vent flow rate, i When a containment purse occurs through one Inch /two inch vent valves to the South Yent, a grab sample will '>e analyzed for noble saa ac-1 tivity, and the 'setpoint for the containment t purse will be calculated per this section. This , setpoint will be compared to the utsting - ' monitor setpoint. ]E the'calculatad con- ' tainment purse setpoint is less than the exist-lag setpoint, M,the setpoint will be reduced to the new value. lE the salcu-lated containment purse setpoint-1: greater than t the salsting setpoint, M the existing ' setpoint will be maintained. At the completion of the contalament purse, the setpoint will be Ener5 H.P. t
, Date Rev. j
-U-.
l : en s !
,._L.~,;. "
- . . _ , , , , , . . , _ . . , u- . . _ . _ , . .. , _ , . - . _
restored to the monitor setpoint that existed immediately prior to the containment purse. SYSPyg ,g 5 (VF,waj[$00][%,) [1.2149E+09)q( Chv)( Ki ll ( ~4}' ' a SYSPyogg 5 [VF,wa)[3000][%,) (1.2149E+09)R( C hv)( L i+1. lMi )) I2'3) where: r SYSPyaw, = South Vent Setpoint - Noble Gas Whole Dody (pCi/ce)- ! SYSPyggg = South Vent Setpoint - Noble Gas Skin (pCi/ce) VFswa = Fractional contribution to site boundary noble gas dose rate from the' Unit's South Vent as calcu-lated in equation 2-8 or 2-ta (unit-i less)
$00 = Total body dose rate limit (mrem /yr) '
3000 = Skin dose rate limit (mrem /yr)
%, = Total noble 'sas activity from each unit South Vent srab sample l
(pCl/cc) 1.2149E+09 = Conversion factor '
=
(1.lE-05 sec/m')(Id'pCl/pCl)(234,000 cfm)(k min /sec)(2.832E+04 cc/ft s ) (2-6)- l ,
, where:
8 l.lE-05 sec/m = highest annual average rela-l . tive concentration (NE sector) i Engr ' ! . H. P. Date l_ ' f Rev. ~ [ - 24 b%
. , _ ,.w - e.- w v., # ~ .,_y ,.w -
. . _ . ~ - --- -.- . . - . - - - . - . . . - ~ - _ - . - - _ _ _ _ _ - - _ - - - .
o l
- I 108 pC1/ 4 1 = units conversion 234,000 cfm = maximum South , Vent now rate i i
h min /sec = units conversion 2.832E+04 cc/ft' = units conversion C, 3 = concentration of noble gas s l\ l l nuclide 1, as determined by radionnalysis of South Vent grab sample ;
, (MCl/cc) j Kg. = total body dose conversion factor for noble gas nuclide 1 (mrom/yr per-l pCl/ms, from Table 2-1).
Li = Beta skin dose conversion factor for - 1' noble gas nuclide 1 (mrom/yr per pCl/ms, from Table 2-1)- ' % = Gamma air dose conversion factor for i
- noble as nuclide 1 (mrad /yr por- j pCi/ms, from Table 2-1) i 2.2.3 Noble Oas Etnuent Fractleed Contribution The noble gas effluent fractional contribution is calcu-4 lated monthly using the results of the'gmb samples per. -
formed in accordance with ODCM 13.3-3.- The results. of l' this calculation are used in equations 2-1, 2-2,' 2-4, and 2-5. This methodology assumes *that the total body dose is the limiting factor for noble ass releases. ) o If equations 2-1, 2-2, 2-4, and 2-5 show that the sida ! dose is ilmiting, fractional skin doses should be sub-
, stituted for'the whole body values used in equations 2 . '
7, 2-8, and 2-ta. e i H. P. ; Date Rev. . h$
. . . . - , . . . , . - , . , - - - , - - . _ . . , - ~ . - . - . . - - , - - - - . + . . , . . . . , - - - .,.,.-.~,-.-.-.--..r
m O 2.2.3.1 Calculation of VFgyno, VFwync, and .
., VF ygg g NYNC
- 4(C igy)(K i ))
4(Cggy)(Ki ))+4(Cigy)( K,)]+4( C ssy)( i Ki )} I2U) VF 4(C i uv)(K ll i ayya = 4(C )( )]44(Cam)(%)]+4(Cusv)(N)] ( 2'8} 4(C issy)(Ki )) aswo " 4(Cggy)( K3 ))+4(C igy)( K g))+4(C ssy)( i K t)1 (' } where: YF gwga = fractional contribution to site bound-ary noble gas total body dose rate from the North Vent (unitiess) VF uvNo = fractional contribution to alte bound-ary noble gas total body dose rate from the Unit i South Vent (unitiess) VF yga = fractional contribution to site bound ~
. ary noble gas total body dose rate from the Unit 2 South Vent'(unitiess)
Cggy
= concentration of noble gas nuclide i as determined by radionnalysis of North Vent grab }
sample (Kl/cc) Ki l
= total body done convepslon factor for noble gas radionuclide 1 (mrom/yr per pCl/ms )
Cigy = concentration of noble gas nuclide 1 as determined by radionanalysis of Unit !- l South Vent grab sample (Kl/cc) C asy-
= concentration of noble ses nuclide 1 as determined by radionanalysis of Unit 2 l
South Vent grab sample (41/cc) ' Engr H. P. osi. ' 1 Rev. - l
=,
o
.2.2.4 Noble Gas Efnuent Default Setpoints ,, This methodology may be used when grab sample resu ts from either the North Vent or the South Vent do not 3 Identify any radionuclides. This methodology is based on expected release concentration ratios as outlined in section 11.3 of the Limerick FSAR.
2.2.4.1 North Vent Noble Gas Monitors (RY26-075A-3 and RY26-0738-3) The default setoolat for the North Vent noble gas of-f)nent monitor is set at or below the NYSPyan value.
$00l1.15E-6)
N oDN 8 [8.90E-1)NyJ1[4.sur.-9] [3.440 (2-9) s 3.45E-5 pCi/cc - where: NYSPM oD = Default North Vest Setpoint - Noble - Ges. (pCl/cc) 8.90E-1 = Default fractional contribution to site boundary noble gas total body dose rate from the North Vent (unitiess)
- 4.30E-9
( 4.30E-9) +( 5.31E-10) where: 4.30E-9 = Summation of the North Vent con-centration of noble gas nuc!!de i , multiplied by the corresponding whole body dose factor 8
~ (MCl)(mrem)(m )'
. (cc)(yr)(pci) ,,
Engr H.P. Date
. Rev.
i J i
O' 5.31E-10 = Summation of the South Vent (Unit 1 .l
& 2) concentration of noble gas
nuclide i . multiplied by the cor-responding whole body dose factor
~ (Ki)(mrem)(ms ) -
3
. (cc)(yr)(pCi) - ,, .
Ref; a) Based on expected annub ' release from FSAR Table 11.3-1 ' b) Based on maximum North Vent flow of 664,000 cfm and South Vent flow of 234,000 cfm for Unit I and Unit 2 vents c) CDCM !! Tabla 2-1 l 500 = Total body dose rate limit (mrem /yr) 1.15E-6 = Total noble gas concentration from North Vent (pCl/cc) Ref: a) Based on FSAR Table !!.3-1 b) Based on maximum North Vent flaw rste of 664,000 cfm. 3.4475E+9 = Conversion factor
" (pCl)(cc) "
_ ( m')( pCl) Ref; a) ODCM !! equation 2-3 4.30E-9
= Summation 02 the North Vent concentration of noble gas nuclide i multiplied by the corresponding whole body dose factor
)
~ (pCl)(mrom)(ms ) - '
(cc)(yr)(pCi) . Ref: 1) Based on FSAR Table 11.3-1
- 2) Based on maximum North Vent flow of 664,000 cfm
- 3) ODCM 11 Table 2-1 Ensr H.P.
Date
. . Rev. ., -)
. o
]
2.2.4.2 South Vent Noble Gas Monitors (RY26-185A-3, l RY26-285A-3, RY26-185B-3 and RY26-285B 3) The default setpoint for each Unit's South Vent ! noble gas effluent monitor is set at or below the SYSPyao value. l SYSPyan (2-10) s ((5.49E 1.2 Hysyg2.62-10] 2][500][7.14E-8] s 6.09E-6 pCi/cc where: '
, SYSPnod =. Default South Vent Setpoint -
Nobie Oss'(MCl/cc) ; 5.49E-2 = Default fractional contribution to site boundary noble ans total body l dose rate from the South Vent (unit- I less) l 2.65E-10
" (4.30E-9)+(5.31E-10) where: '
2.65E-10 = summation of each Unit's South Vent concentration of noble gas nuclide,i multiplied by the cor- . t responding whole body dose factor + s t
" (MCl)(mrem)(m ) -
. (cc)(yr)(pCl) _
l
- 4.30E-9 = summation of the' North Vent con-centration of noble as nuclide l' multiplied by the corresponding whole body dose factor ,
s '
"(MCl)(mrem)(m ) -
_ (cc)(yr)(pCi) . I h Date Rev. .
+ -
29 i
+
+
l^ i l 5.31E-10 = summation of the South Vent l . (Units 1 & 2) concentration of noble ; s sas nuclide i multiplied by the cor- , responding whole body dose factor
* ~ (Kl)(mrem)(ms ) " ;
l . (cc)(yr)(pCi) , L $ , l 'Ref; a) Based on expected annual releases < l from FSAR Table 11.31 t b) Based on maximum North Yent flow of 664,000 cfm and South Vent flow 1 of 234,000 efm for Unit I and Unit 2 Vents
^
c) ODCM II Table 2-1 .l . L300- = total body dose rate !!mit (mrem /yr) i 7.14E-8 = total noble gis concentration from - South Vent (,uCl/cc) 1 Ref: a) Based on FSAR Table 11.31 b) Based on maximum South Vent flow of 234,000 cfm) - 1.2149E+9 = Conversion factor
" (pCl)(cc) "
l t I . (m')(pCl) Ref: ODCM !! equation 2-6 2.65E-10
= Summation of each Unit's South Vent concentration of noble gas nuclide i multiplied by the corresponding whole '
body dose factor
~ (KI)(arem)(m8 ) '
. (cc)(yr)(pCl) .
P Ref: 1) Based on FSAR Table !!.3-1
- l. 2) Based on maximum South Vent flow of 234,000 cfm for Unit 1 i i and Unit 2 wnts
- 3) ODCM !! Table 2-1' 'l o
H. P. ' , Date *
. Rev.
tip 9
- - . .-. ,- . . . - - . . . - - - _ - _ - . . . - - , , _ , - . . . - - , - - - - - - . . . - . - . . - . ~ -
.pg. --- O e 2.2.5 Wide Rt.nge Accident Monitor
.sle Gas Effluent Monitor (RIX26-076-4)
The Wide Range Accident Monitor (WRAM) noble gas total efnuent channel monitors the noble gas effluent from s the ' North Vent. This monitor has Mala Control Room An. nunciation as well as an isolation function on the pri ~ ' mary containment purge and vont valves. The isolation setpoint value of s 2.1 Kl/cc specified in Techn!- cal Speelfication Table 3.3.2-2 is based on the accident dose limits for containment purge during an accident (kef: FSAR Section 1.13). For' routine operations the total effluen' alert and high setpoints are based fMn the methodology of Sections 2.2.5.1 and 2.2.5.2. The setpoint units are in microcuries per second using the
. two unit maximum North Vent flow rate. The total of-fluent channel High setpoint is set at a value less ihan.
i or equal to (en times the Alert setpoint (not to escoed the 2.1 Kl/cc equivalent using the two-unit maximum North Vent flow rate).. For containment purge operations, the high setpoint is based on an isot,opic analysis of the containment atmosphere (Ref. Section 2.2.5.3), These values are always more conservative than the Techalcal Specifica-tion Table 3.3.2-2 required value of 5 2.1 Kl/cc. If the calculated setpoint value is less than the exist-Ing monitor setpoint, the setpoint will be reduced to En H.F. S' Date ' Rev. I
%9
1-the new value. If the calculated setpoint value is s greater than the ealsting value, the setpoint may remain at the lower value, or increased to the new value. 2.2. 5.1 Routine Operations Alert Setpoint betermination e For routine operations, the Alert setpoint for the WRAM Noble Gas total effluent channel la set at or below the lesser of the NYSPNon of ~ NYSPNosx value. The Alert setpoint 1s not ! to exceed 1.1 E-04 pCl/cc equivalent, using the ! i two-unit maalmum North Vent flow rate, per LOS ' FSAR Table 11.5-2. i. NVSP "V"8 # NOM s -{3.4475 E+09J4(C i uy)(Ki)) (2*11) 1
)
IYF,ygo)[3000][DCw] s Nc5K I [3,4473 g+ggjg(Cg)(L;+},jg)j' (2*I2)
- where:
NVSPyou = North Vent Setpoint - Noble Gas Whok Body (MCl/cc) NYSPyasg = North Vent Setpoint - Noble Gas Skin (pCl/cc) ' VFyyya = Fractional contribution to alte- i boundary noble gas dose rate from the
' North Yent as calculated in equatiott '
2-7. (unitiess). 500 = Total body dose rate limit (mrom/yr) Eny H. P. Date Rev.- - '
-M-l l ,-
v..,,. .
,, . - - , , , -. , - . . ~ , . v,.-. ... - , -. . . - , -. - . - ~ , - , , , . ,.e - , - . -, ,.,- -,.,,- ,- <
1 3000
= Skin' dose rate limit (mrem /h) .
v ECm = Total noble gas activity from North Yent grab sample (mci /cc) . l 3.4473 E+09 Conversion factor
= 8 P (1,lE 05 sec/m )(10 pC1/pCl)(664,000 cfm)(k min /sec)(2.832E+04 cc/fts ) (2-13) where:
l 1.lE-0$ sec/m8 = highest annual average - relative concentration (NE , Sector) i 10P pCl/pCl - valta conversion 664,000 cfm = maximum North Vent flow I rate for two unit operation ~
- l hmin/sec = units conversion -
2.832E+04 cc/ft' = units conversion i Cm = concentration of noble ans nucilde i as determined by radionnalysis of North Vent grab ' sample (pCl/ce) L % = Total body dose conversion factor-for noble gas nuclide 1 (mrom/yr per pCi/m' from Table 2-1), , Li = Beta skin dose conversion factor for noble gas ~ nuclide 1 (mrom/yr per ' pCl/m8 . from Tabis 2-1), t
% = Gamma air dose conversion factor
- for noble as nue11de 1 (arad/yr per pCl/ms , per Table 2-1), i l sogr -
H.P. nai. - Rev. ; t b% a _ _ , _ _ _ . - _ - - - - - - - - - - - - - - - - ^
l
~O 4
The setpoint values are converted from #Cl/cc to mci /see using the maximum two unit North Yent flow rate: s a NYSPygg = [NYSPyag) [3.lME+08) (2-14) NYSP Tasx = [NYSPNosx) !3.IME+04) (2-15) where: NYSPy n = WRAM totti emuent channel North Vent Sepoint - Noble Gas Whole Body ( A.'sec) NYSPasu = WRAM total emuent channel North Vent Setpoint - Noble Gas Skin (pCl/sec)
, NVSPN on = North Vent Set ant - Noble Gas Whole Body (pCl/cc) .
. EngrM H.P. /44 .
Date t // l Rev. - 34 t> 9
. . - . - - . _ . - - . - . - - - - . - - . ~ . - - - . _ . - - . - _ .
*f e
NYSPN csx
- North Vent Setpoint - Noble Gas Skin (#Cl/cc) i . !
3.134E+08 = Conversion factor (cc/sec)
= ( 664,000 scfm)(hdn/sec)(2.832E+04 cc/ft') (2-16)
, 2.2.5.2 Routine Operations High Setpoint Determination For routine operations, the high setpoint for .
the WRAM Noble Gas total effluent channel Is set ' at or below ten tlines the lesser of the routine operations NYSPaws or NVSP gg , value. , , 9 i NVHPnws = (NYSPgws) (10) (2-17) NVHPnm = (NYSPag) (10) (2-18) + wlere: . NYHPnws = WRAM total effluent channel North Vent High Setpoint Noble Gas Whole Body (MCl/sec) NVHPnm = WRAM total. effluent channel { North Vent High Setpoint Noble Gas !
, Skin (MCl/see)
P/j!Br i cate Rev.
.upt to 4 F
1_u__u___.______.___. _ _ _ _ _ _ _ _ _ _ _ _ _ _._____z___.__.-. _ _ _ _ - _ _ . . . . _ . - . . - . - _ . . . . - . -. . -
_ --_. .- . . _. .. _ . . _ . . _ _ _ _ - - . . . _ _ ~ . - - . . _ _ . _ . - _- _ . _ _ _. - i, . 1 i 1 I l t NYSPnws = WRAM total effluent channel North Yent Serpoint - Nob'le Gas i Whole Body (pCl/sec) { t- i, l , NYSPasg = WRAM total effluent channel i ; North Vent serpoint - Noble Gas Skin (pCl/sec) ' l . j t 10 = multiplication factor to calculate ' High value (unitiess) I 2.2.5.3 High Setpolat Determination - Containment Purse Operations During routine puty operations via North Stack. the setpoint will be determined prior to lattiation 1 of the purse based on the containment noble gas , grab sample required by ODCM 13.3-3A. The WRAM ' i high setpoint is set at or below the lesser of the - WRSPyap,, or WRSPyapsg value. At no I times will the setpoint be higher than 6.58'E+8 '
#Cl/sec (Ref. Specification Table 3.3.2-211mit of i s 2.1 NCl/cc converted to #Cl/sec (2.1 #C1/cc .
is based on maximum 2 unit North Vent flow rate). WRSP "8 NGPWR s [1.10E+1] gE {(C )(K )] g (2 19V # WRSP [YFmN 1[3000][DCw] yopsg s (3,39g,3] 3 ;(g )(g,3,3g,)j (2 20) l where: , i WRSPy opy = WRAM Purse Setpoint - Noble cas Whole ' Body (MCl/sec) - l Eny H. P. Date l
~
Rev. ! 36 - l 1 b%
, ..n, - - - ,.., , - - . - , . - - - -- , , . - . ~ , . , . , - . - . . , , . - . . , . , - , , - - , ,
g WRSPNcPsx = WRAM Purge Setpoint - Noble Gas skin L 4 1/sec) VF uyua = Fractional contribution to site bound-ary noble gas dose rate from North Yent as calcu-lated in equation 2-7 (unitiess)
$0'0 = Total body dose rate limit (mrem /yr) s 3000 = Skin dose rate limit (mrem /yr) -
ECu = Total noble ses activity from containment grab sample (pCl/cc) 1.10E+1 = Conversion f actor S
= (l.IE-5 sec/m )(Id'pCl/#Cl)(k min /sec)(2.832E+4%) (2 -
472 %see.ft L where: , l.lE-5 = highest annual average relative concentra-s tion (sec/m ) (NE sector) 10' = units conversion (pCl/pCl) h = units conversion (min / sac) 2.832E+4 = units conversion (cc/ft') l 472
= units conversion , sec 'N-ft , .
Cg = concentration of noble gas nuclide 1 as determined by radicanalysis,of containment grab sample (pCl/ce) ; Ki = Total body dose conversion factor for noble gas l nuc!!de 1 (arem/yr per pCl/mi from Table 2-1) Li = Beta skin dose conwrsion factor for noble gas g nuc!!de 1 (mrem /yr per pCl/ms from Table 2-1) Mi = Gamma air dose conversion factor for noble gas l4 nuclide 1 (arad/yr per pCl/m a, from. Table 2-1). En ! M. P. Date " '
. Rev.
b
. e.
i I J I 2.3 Gaseous Erduent Dae Evaluation *
- i The gaseous efnuent dose evaluations are generally per.
formed .using the computer based RM 2]A report processor. 4 '. The following sections describe the computational models, . assumptions and bases for the computer model. In the event i i that the computer model is unavailable for the required dose - i analysis, the dose analysis will be performed by manual cal-
)
culation using the same methodology as the computer based a report processor. " J Monthly dose calculations are based on limiting sector aver - l age annual meteorological dispersion parameters. ' This cal- . culation is performed using a senarlo of meteorclo81 cal con-ditions which yield the limiting meteorological dispersion value required. For the noble ' gas monthly dose calcula-tions, ernuent release data are based on the latest grab sample tnalysis for radionuclide composition and the hourly ' average efnuent monitor response for total release ac-tivity. For the lodine and particulate abnthly dose cal- t culations, the effnuent release radionuclide composition r and release activity are based on the continuous composite samples for the time period of the dose calculation. The quarterly dose calculations are a summation of the ap- . plicable monthly dose results. t c Enstd
^
H.P. F4 Nv' 33 l-l ,. , f
._ . L
j o The annual dose calculations are based the'meteoroksical conditions concurrent with the effluent releases. Thi meteorological conditions are based on the year's finalited meteorological data. Wind direction, temperature lapse rate, ambient temperature, ground level windspeed,'and release elevation windspeed are provided for each hour of the year. The meteorological dispersion values (X/Q,
, depleted X/Q, and D/C are calculated for each hour and linked with the corresponding release data. The ernuent release radionuclide composition and activity are based on the same parameters as the monthly dose analyses, l
, 2.3.1 Site Boundary Dose Rate - Noble Gases ODCM 13.3.2.a limits the dose rate at the $1TE BOUNDARY due to noble ass releast to s 500 mrem /yr total body and 5 3000 mrom/yr skin.
Radiation monitor alarm setpoints are established to ensure that ti.cs release limits are not ex-coeded. In the event any gaseous releases from
- l the station results in an alann setpoint being ex '
coeded, an evaluation of the SITE BOUNDARY dose rate resultin's from the release will be performed using the following methodology. . H.P. d
. Date !
Rev. ! 39 i
'O l
1 As appropriate, simultaneous releases from the North and 4 South Vents will be considered in evaluating compliance with the release rate limits.of ODCM 13.3.2.a following
.s i any releases exceeding the above prescribed alarm set-
- I i
points. Monitor indications (readings) may be averaged over a time period not to exceed 13 minutes when 1 determining noble gas release rate based on correlation -
\
of the monitor reading and monitor sensitivity. The 15-l min averaging is needed to allow for reasonable monitor respome to potentially changing radioactive materia! l concentrations and to exclude potential electronic j spikes in monitor readings that may be unrelated to radioactive material releases. As identified, any elec-l 1 tronic spiking monitor responses may be excluded from the analysis. NOTE.- For administrative purposes, more conservative alarm setpoints than those required to meet 10 CFR 20 Dose Rate limits may be imposed. I However, conditions exceeding these more limiting alarm setpoints' do not necessarily indicate
'I i
radioactive material release rates exceeding the l
. dose' limits of ODCM 13.3.2,a. Provided actual releases do not result in radiation monitor In- .
dications exceeding values based on the dose rate 1 Engr H. P.
. Date ~
i Rev. t l
- tb 9 '
I limits of ODCM 13.3.2.a. no further analyses are l ; required for demonstrating compliance with the limits of ODCM 13.3.2.a. ! u l , i ( , The site boundary dose rate from noble gas effluent j l releases in the event of a noble gas effluent setpoint l exceeding the value specified in ODCM 11 sections 2.2-1 (or 2.2.4.1), 2.2.2 (or 2.2.4.2), and 2.2.10 is calcu-lated using the methodology stated below. This meth- l L odology is based on worst sector (NE) annual average , l l' meteorological dispersion but, if further refinement is required' to meet the requirements of ODCM 13.3.2.a ac. l
~
tual meteorological dat; from the time period of concern - may be used to calculate actual meteorologi'.al disper- [ sion. 1 D,pra = (53.882)(X/Q) f[ [(F,,y)(Q,)+(Fgy)(Q uv)+(T:sv)(Qasv) i ) Ki ] (2-22). -t i l l Eny H.P. Date H f , Rev. 1 ' L h
0
~
( )(Qay)+( F ,y)(Q ,y)+( F,,y)(Q,,y) 3 ] L, } '+
- 3 it i Desx = (53.882)(X/Q)
_ , (SF)f [ [( Fw)(Q,w) +( F ,y)(Q,3,y),( p,,y)(qt,,y) )g ( g, g ;) } _ 3 (2-23) where: Da Total Body Plume Dose Rate (rem /hr) Dp,x = Skin Plume Dose Rate (rem /hr) 53.882 = Units conversion factor
, , ', "[,# ,
X/Q = 1.lE-05 highest annual average relative con-centration (NE Sector) (sec/ms ) Fw = North Vent Flow Rate (cfm) Qwi = concentration of noble gas nuclide i during period of release from North Vent (pCi/cc) F isy = Unit i South Vent Flow Rate (cfm) ! Qit ,y = Concentration of noble gas nuclide i during period of release from Unit i South Vent (pCi/cc) F,,y = Unit 2 South Vent Flow Rate (cfm) Qasy = Concentration of noble gas nuclide 1 during period of release from Unit 2 South l Vent (pCl/cc) Engr H. P. Date Rev. 42 - b%
l . l l
?
{ Kg = Total body dose factor for noble gas. nuclide 1. Values listed in Table 2-1
, l s .
" mrem-ms ' )
, pci-yr s L = Skin done factor for the beta contribution for noble gas nuclide 1. Values are listed - l'
"**"s' e
in Table 2-1 pCi-yr ! s s ' 1.11 =
-- the average ratio of / issue to air energy absorption coefficient,t (arem/ mrad) (Ref: .;
Res. Guide 1.109 Sect'on 2.2) SF = , 0.7 is the attenuation factor that accounts . for the dose reductior, due to shielding pro- l vided by residential structures (dimension- + less) (Ref. Res. Guide 1.109 Table E-15) , M3 = Oamma air dose factor for. noble gas nuclide i ! 1. Values are listed in Table 21 i
" mrad-m8 '
s pci-yr s c 2.3.2 Site Boundary Dose Rate Radiolodine and Particulates . ODCM 13.3.2.d limits the dose rate to s 1500 mrem /yr to any organ (inhalation pathways only) for 1-131, I-133,
- tritium, and all radionuclides in particulate form with i
half-lives greater than 8 days in gaseous effluents. Compliance with ODCM 13.3.2.d will be determined monthly ! by performknce of ODCM !! section' 2.3.4. As appropriate, simultaneous releases from the North and South Vents will be considered in evaluating compliance with the release rate limits of ODCM 13.3.2.b. Release - - activity is based upon the result: 'of the continuous ' Engr H. P. , Date l h.
, 43 ,
b%
, . . , _ . , , _ _ _, _._,__6_ ,,y,_ , , ,, . _ , . _ . , ,G_.,
O composite sampler analyses perfor-A in accordance with ODCM 13.3 3. l , This methodology is bastJ on the worst sector (NE) an- L nual average meteorological dispersion but, if further
- refinement is required to meet the limits of ODCM t i
13.3.2.b, actual meteorological data from the time per-lod of concern may be used to calculate actual meteorological dispersion. k 2.3.3 Noble Gas Air Dose i ODCM 13.3.3 timits the air dose due to noble gases r released in-gaseous effluents (from both reactor units) to areas at or beyond the SITE BOUNDARY to: s 10 mrad samma for any quarter i s 20 mrad beta for any quarter s 20 mrad gamma during any calendar year s 40 mrad beta during any calendar year As required by ODCM 13.3.3.1 Surveillance Requirement, ' these doses are calculated at least once per 31 days . l using the results of the most recent grab samples fut isotopic composition performed in accordance with ODCM , 13.3 3. Due to the incorporation of the ALARA philosophy in the design and operation of the Limerick Engr H. P. - Date
.u. ' Rev.- '
%Q s.y. m - - .._.v..-.,.. ~ , ._._1 .. ,., _ _ _ .,-._. ,, , . . . ,,_.. _ . __ _ _ _ _
.f f , , . .
i: , t!Tluent systems, release point grab samples may hot - L *s, l identify any radionuclides. Total release acitvity is - !. i [ - based upon the hourly average effluent monitor response. l g, ,. .. 1 1 As identified, any electronic spiking monitor responses - s may be excluded from the release activity analyses. ' The - - monthly dose calculation is ~ performed using the most - - limiting average annual meteorolopcal dispersion : i
.a values. ' The quarterly doses -are based on the summation -
- of the applicable monthly results. ' The annual dose.. l' 5
' calculations are based upon actual release;meteorologi-- '
- cal conditions as described in'Section 2.3.5. The:
mor.thly dose calculations are performed in'accordance with the methodology. and calculations below.. l D win = (O.I14)(l.1E-5)(472) { [(F yy)(Cm)4(Fay)(Cigy)+(F asv)(Cusv)-] M g.(2-24) l D,ga = (0.ll4)(1.1E-5)(472)' y -[(Fyy)(Cary)+(Fuv)(Ciuv)+(Fagy)(Cusv) ]. N (2- 5) 3 3 where:
- b Dgga = Gamma air dose from noble)sas releases (rad /hr) 1
- ' l Dwa = Beta air dose from noble gas :
releases (rad /hr)~ l < l En i H.P. l Date i
. Rev.
o - 45 (e . t .+ . .. . . . --.l. -
.3 1
1
'O.lldi = Units conversion' ,'h rd i 1,lE-5 W Highest average annual relative con-
~
, ceraration (NE mtor), (sec/ms)-
472 = Units conversion
.%sec-it , .
Fw = Average North Vent flow rate for .
/
period of release (cfm) .
.]
Cm = Concentration'of noble gas nuclide i from North Vent effluent (pCi/cc) 1 F 3,y< = Averase Unit _ l' South Vent flow rate ! for period of release (cfm). C issy = Concentration of noble ' gas nuclide i from Unit 1 South ; Vent effluent. (#Ci/cc) . F3 ,y = Average Unit 2 South Vent Rw rate ' for period of release (cfm) 4 C usy = Concentration of noble gas nuclide i from Unit 2 South ' Vent. effluent i (#Ci/cc)
% -. = Gamma air dose factor for noble' gas nuclide 1. ' Valves are listed in Table 2-1
_[
" mrad ms *
, pCi-yr ,
I, N3 = Beta air dose factor for' noble gas nuclide I
'i. Values are listed *it Table 2 l
' mrad-ma ' ~
c pci-yr , i 1 2.3.4 Radiolodine and Particulate Dose Calculationi ODCM 13.3.4 limits'the dose (from both rewtor units) to
- a MEMBEht OF THE PUBLIC from I-131,1-133, tritium, and -
all radionuclides in particulate form with half-lives Date n /// Rev. - 46 -
-b1
n l 1 greater than a days in gaseous effluents released to . areas at or beyond the SITE BOUNDARY to: l
, 515 miem to any, organ during any
, calendar quarter ,
a s 30 mrem to any organ 'during any calendar year L As ' required by ODCM 13.3.4.1 Surveillance Requirement. l. L-l;, ,
' these doses ~ are calculated at least once 'per131 day l
- using the~ results of 'the continuous composite sample: ;
, analysis performed in accordance;witht ODCM 13.3-3. Due h
i
'to the incorporation ~ oflthe: ALARA philosophy in the L
, design and operation of tho' Limerick effluent' systems, ~l 5
these composite samples' may not identify any radio : s L nuclides. Total release activity is based upon detec- 1 4 table concentration of the continuous composite samples' q-p and average appropriateL vent flow during the ' sampling . period. The monthly dose calculation is performed uilng, the most limiting average annual meteorological 'disper- 'i' slon values. ~ The ' quarterly doses; are based on the sum- .
.mation of the applicable monthly results. .The annual dose calculations are based upon actual release-meteorology as described in Section 2.3.5.. Theimonthly dose calculations are performed in accordance with'the methodology'and calculations below. . Total organ dose is ~
/ obtained by the summation cf the organ dose from.esch
- l. pathway for each receptor. #
En H. P. Date (- Rev. .j
)
1
~
.st
.c i
2.3.4.1 Ground Pathway CPAR = ( 3.6E-6)(472)(l.82E-9)
, i,Na [(Fuy)(Q yy)+(F i '
av)(Qi uv)+(F3 ,y)(Qa,y)+(Fas)(Qms)](DF:x3 )
~
i (T ) (2-26)
' 2.3.4.2 Vegetation,' Meat, Cow Milk,' and Goat Milk- Pathway '
Dypra = (3.6E-6)(472)E
~ , [.(Fgy)( Qi gy) +( Fuv)( i Q ny)3 +( F y)( Qagy)( Fas)(Qms)](l.1E-5)(DFgg3 i .)+-
, , . . ~
_ (T,) [i,,[(Fuy)( Qi gy) +( Fay)(Q i nv)+(F ,y)(Qagy)+(Fas)(Qms) i ](l.82E-9)(DFgggp) ( 2-27) ! 2.3.4.3 Inhah tion Pathway. Dipra = (3.6E-6)(472)E
, [(Fyy)( Q igy)+(F uv)(Qi nv)+(F ,y)(Qa,y)+(F 3 as)(Qms)](1,IE-5)(DFgg i ) +
(T) i _ ,, ,[( Fgy)(Qi gy)+( Fay)(Q,gy)+(F ,y)(Qugy)+(F&g)(Qims) ](l.0E-5)(DFx33) ( 2-28)' where: l Engrd . l H. P. Date // Rev. [
~'
95 % ls l, _ , _-
g
. .4 Depra = dosi from ground pathway due to release of peticulates'and lodines (rem); '
DVPAR = dose fron vesetation, meat, cow milk, . l i and goat mi:k pathways due to releases of. particulates, loo!wes, and tritium (rem) ' .] i C DIPAR. = dose from inhalation pathway due to
~ release-of particulates, lodines, and t
' tritium (rem): ~
-s
'3.6E-6 ' = units conwrsion- fahtor h','", ]
,. ' \
472-
. = units conwrsion factor "%seu-(t. s ,
1.82E-9 = highest averase annual deposition (ESE sec . tor) [m , ,.
-{ = summation for each release time period-(unitiess) -
Fw = average North Vent flow rateLduring release (cfm) Qw- i = concentration of nuclide i from North Vent effluent (pCi/cc) . Fav
=
average Unit i South Vent flow rate during release'(cfm)
- Qi sy =
concentration;of nuclide i frorn Unit i 1 l- South Vent effluent (pCi/cc) p = F sv averase Unit 2 South Vent flow rate during release (cfm). i
. '\
Qu,y = concentration of nuclide l' from Unit.2 4 South Vent effluent (pCi/cc) Fms - average Hot Maintenance Shop flow rate
, during release (cfm) J Qm = concentration of nuclide i from Hot l t
Maintenance Shop effluent (pCi/cc) - / Engr i H. P.' I Date i
, Rev.
1 i l l i o - I
DFig, = - dose factor for organ . type k, age . --y , group 1, pathway number n; dose factors are - based ~on results of a computer program that is based on and is similar to the NRC pro-gram GASPAR; results from this program pro-vide input data in the form of a lookup . table - values of DFy, are provided ,.
-in Table 2-2.
1 isotope .oumber (1 through 35) (3 through 17 are noble gases) +
, k = organ type (1 through 8,fwhere total body = 1, GO l tract = 2, bone = 3, liver =' 4, kidney = 5,
. thyroid = 6,= jung = 7,~ skin = 8) "
. I = age poup (1.through 4, where. adult = 1. teen = 2, child '= 3, infant = 4) n = pathway number (l through 7)
T, a ! time duration of release (hrs) . 1.lE-5 = highest aserage annual relative concentration i
-(NE sector) (sec/m8) 1.0E-5 = highest average annual relative depleted con-i centration (NE sector)-(sec/m 8) .
l 2.3.5 Anntal Dose ' Evaluation-CDCM 13.6 requires an Annual Dose evaluation be per-formed and reported in accordance with Regulatory Guide 1.21 in the Semiannual-Radioactive [.ffluent Release ; Report submitted 60 days after the first of each year. This dose evaluation is processed by the computer based
~ RM-21A report processor. In the event that this com .
puter model is unavailable, this analysis will be per-formed using the same methodology. The liquid portion - of this annual dose calculation is described in Section Date - Rev.
. 50 - .%9 m
,. Le 1 i
.1.3 of ODCM II. The annual'enseous dose calculatlon uses the same general methodology described'.in Section
'. J 2.3.1, 2.3.3, and 2.3.4 ;with the exception. of meteorol - j osy; which is based upon sector average atmospheric dis-( y .
persion 'valuest using the guidance 'of Regulatory Guide ~-
]
1.111 (Section C le). Finalized hourly values of wind V . direction, ground lew! and release' elevation wind ; speed, ambient temperature, and temperature lapse rate ' (for P-G stability class)' are provided annually using the' instrumentation specified in ODCM 13.1-1. These-
.)
values are calculated for each hour and linked to the corresponding hourly. averaged effluent release' rate. j Doses are then calculated for each hour at the various. p receptors of Inte' rest (depending upon release direc - tion) . - Radioactive material release activity is calcu-L lated as -described in Sections 2.3.3 and'2.3.4. - Dose at - each receptor is accumulated for the year, and the' maxi, mum dose for plume, inhalation, and: ingestion pathways ! l are reported. , The gaseousLeffluent dose receptors are - 1 t. listed in Table 2-4 and the dose is calculated using the ' methodology below. - l
. . I I
1 Engrd H. P.- Ditt & Rev..,f b%
,
- m , . - . = -, - p #e ,.-. - , +
~ >
e l l J 2.3.5.1 Plume Pathway ' DPt.NcA " (3.6E-6)(4f2){(X/Q),, [(F yy)(Q,gy)+(F uy)(Q uv)+(F i y)(Qssy) as i 3- * [ m [,(*M)(d')/8 h opyg 6 g.
~ 2.3.5.2 Ground Pathway' . "
as " (F gy)(Qgy)+(F i av)(Q iuv)+
~ '
E LDGPARA=( 3.6E-6)( 472) ( D/Q), 'I"2 (DF m )(T,) (2-30) _ (F3,y)(Q;3,y)+(Fas)(Qms) i n 2.3.5.3 Yegetation, Meat, Cow Milk, Goat Milk Pathway DVPARA=( 3.6E-6)( 472)E
- [ ,gr 1((Fyy)(Q ny).+(F y)(Qusv)+(F ,y)(Q ,y)+(Fas)(Q ms)}[X/Q,](DFigio) -
i g 3 i3 4= i , 3
~
- _ ( T,) -
. . i=u[(Fgy)(Qgy)+(F i uv)(Q iuv)+(F ,y)(Qa,y)+(Fas)(Qas) ][D/Q),(DFthin) !
t. (2-31) i 3 l .i I L- Engr i-H. P. 6- " Dat. a/r/q Rev. [
- $2 - .
i S b1 rn- e +- e* e ,e,--g--s-r- m ~ - . = + - - , - - + ,-
l * [ . 2.3.5.4 Inhalation Pathw3y D,p4a4 = (3.67.-6)(472)E _ 3[(,I'Nv)(Q ny)+( i F m')(Q i ssy)+(F a sv)(Qasv)+(Fas)(Qms) ][X/Q),(DF ,) i igg .+ [(Fgy)(Q;gy)+( F isv)(Qitsv)+(F,,y)(Qasy)+(F
. (T as)(Q ims) )[X/Qa.pt ](DF igt
)
-( 2-32) .
where: Dpg, gag = annual dose from plume pathway (rem) D GPARA = annual dose from ground pathway (rem)- D yp4g4 = annual dose from- vegetationi meat, cow milk, and_ goat milk pathways (rem) DIPARA = annual dose from inhalation pathway (rem) 3.6E-6 = units conversion factor em -sec ' 472
= units conversion factor n-cc'
, sec-ft 3 ,
E = summation for each release time period (unit-less) i (X/Q), = relative concentration for time period "t" 8 (sec/m ) Fuy
= averase North Vent flow rate during release (cfm)
Qyy i
= concentration of nuclide i from North Vent effluent (pCi/cc) .
Engr H.P.
, Date Rev. 1 '
F asy
= average U *5 ' South Vent now rate during .. release iefm) --
Q41sv = concentration of nuclide i from Unit i South'
, Vent _ ernuent (pCi/ce)
, F agy
- average Unit 2 South Vent now rate' citing .
release (cfm). - 1 Qasy: = concentration of nucliae i from Unit '2 South t Yent effluent (pCi/cc)
-Ai
= decay. constant of, nuclide i-(sec.2)
, y dr = distance to receptor *r* (m)-
U, - average windspeed for time period "t" ~ t (m/sec) ; DFg;, = dose factor for organ type k, age group 1; pathway number n; dose factors are' .!'
- based on results of a computer program that is based on and'Is similar to the NRC program L
GASPAR; results from this program provide in-put data'in the form of a lookup table - values of DFgj, are provided in Table
". - 2. -
i = isotope number (1 through 35) (3 through 17 are _ noble' gases) i k = organ type (1.through 8, where total body
= 1 GI tract = 2, bone = 3,'11ver = 44 -i kidney = 5, thyroid = 6,' lung = 7, skin -
i 8)' I = age group (l throuk 4, where adult ;= 1. teen = 2, child = = 3, infant = 4) n = pathway number (l through 7) T < i
= time duration'of release (hrs)
F ms
'
- average . Hot Maintenance Shop flow rate -during '-
release (cfm) - ' Qi ms = concentration of nuclide i from Hot Maintenance - Shop effluent (pCl/cc) l ' En H. P. Date - Rev. 54
. .j
7 - . e- e
.)
1 ( J (D/Q), = diposition concentration for time period "t* (1/m 2)-
.,, (X/Qa,,i), = relative depleted ~ concentration for . I time period "t* (sec/ms- )
ii 3 2.4 Gaseous Effluent Dose Projection, ODCM 13.3.5 requires that the : VENTILATION EXHAUST TREATMENT SYSTEM be used to reduce radioactive material levels prior. i to discharse when projected doses ~ from both units to areas ; at and beyond the SITE BOUNDARY.would exceed 0.6 mrem to 'any- < organ;in a 31 day period.
' The appplicable gaseous processing systems for maintsining radioactive- material releases' ALARA' are thi Gaseous-Radwaste Treatment System'and Exhaust Treatment System as delineated in Figures 2-1 and 2-2.
A dose projection is performed at least once per 31-days by the following equation: . a ; Dmaxp = (Dmax/d) 31d' .
' ( 2-33) ' ,
- e where:
[ Dmaxp = maximum organ dose projection for current 31-day period (mrem), . Dmax = maximum organ. dose to date for current-
~ calendar quarter as--determined by equation (2-26) (2-27)' or_. (2-28) ' (mrem)- .
Date 'N ff Rev. .
'1
~ ~
_.-- - - - __.______.__$ . , - . . - . . . ; , , - _..,y,_y, . . . , , , . , . , , ,p,9-
~ d .-
= number of days in current ~ calendar quarter..
at the end of the release. The minimum i time elapsed is seven (7) days. 31d ' = the number of. days of- concern : 3.0' Special Dose Analysis-3.1 Total Dose to MEMBERS OF THE PUBLIC. ODCM 13.3.7 requires that the annual dose or dose commitment to any MEMBER OF THE PUBLIC, due to releases of radioac-tivity and radiation, from the _ uranium fuel cycle'shall be i limited to:~ j
.l 5 25 mrem whole body or any organ except thyroid- '
s 75 mrem . thyroid
~ ODCM 13.3.7.2 Surveillance Requirement requires that cumula-tive dose contributions from direct radiation from opera- ,{
q tions be evaluated when the calculated. dose from the release -
\
of radioactive materials in liquid or gaseous effluents ex - ' ceed twice the lists of ODCM 13.2.3.a,' 3.2.3.b, .3.3.3.a; 3.3.3.b 3.3.4.a, or 3.3.4.b. The direct radiation contri-bution shall be determined by the methodology described be-low. This methodok,gy calculates the dirgt radiation. con- , tribution which then must be added to the dose or dose com-mitment determined in accordance with.scetions ODCM 111.3.1, . s 2.3.3, and 2.3.4= to determine total dose from all pathways. - i Thl,s evaluation of direct radiation contribution is in ac-cordance with ANSI /ANS 6.6.1-1979 Section 7. The error using this method is estimated to be approximately 8% The H 6 Date /
~
Rev.
. ss .
t bN
. ... - - . ._. ~. .
' +
;\
e 1 following evaluation is performed for each receptor of con -
-cern.
)
Don3 =.D.rt.o -D arrrL
, r p -D .
( 3-3) X SKo , i where: Dona. = c' umulative dose ~ contribuilon from direct. radiation at receptor 1 (mrem). Note: Due to the statistics of radiation measurements and to - the conservation of effluent calculations it is~ plausible that Doni J may'. yield a negative value. In this.
. situation the'.value for Don 1 shall be reported as'
- zero(0).-
.D' yrg,og = total dose at Lreceptor of[ interest-(as.
evaluated by TLD measurement) (mrem) . r Note: 'If there is not.a TLD location at the actual receptor location, a more conservative location .will be used to .i evaluate Total Dose. D = mean of the background-dose as Isxo evaluated by TLDs at background sites (mrem),
.i DittrL' = effluent contributiorr to dose (as evaluated in sections 2.3,3 and 2.3.4,1).
m 3.2 Doses Due to Activities'Inside The~ SITE SOUNDARY- " In accordance withlODCM 13.6, the Semiannual Radioactive Ef-fluent Release Report subraitted within 60; days after January 1 of each year shall include'an assessment'of radiation dose. from radioactive' liquid ~and'saseous effluents t'o MEMBERS OF THE PUBLIC due to their-activities inside the SITE BOUNDARY. . Engr H. P. Date Rev. I l~ .- o . _ _ _ . _ _ _ _ _ _ _ _ _ _ _ - _ _ _ _ _ _
'{
]
U
.1 There are three locations 'within the SITE BOUNDARY that are -
- i accessible to MEMBERS OF THE PUBLIC for activities unrelated: l i
g
- to the operation of Limerick station. - These locations are:'
s 1) the ral! road tracks which run Jong t.** riwr within the- ' SITE BOUNDARY;-2) the Limerick Atomic Information Center,~ on Longview Road next to the 500 kV substation; and 3) Fricks Lock environmental laboratory, operated by RMC. Environmental
. Services, Inc. Of these three locations,' the railroad tracks are the closest to ts plant confines. The highest '
i annual ddse for the three locations should be demonstrated ' by the railroad. track locaiion. The following-methodology is used to evaluate dose at the ' railroad trach, Information Center, and Frich. Lock loca- .l tions.
~
This dose assessment is based on the results of the annual dose evaluation as outlined'in ODCM Section 2.3.5, The maximum dose ' calculated'will be reported.
~
DPsax = Dsax *
- 0.25 .
(3-2)
- where:
4 Drsax = Dose to MEMBERS OF THE PUBLIC within the 1 SITE BOUNDARY in Sector T (mrem)i j Dsex = Dose at SITE BOUNDARY in~ Sector T (mrem) Engr M H. P. W g s 90 "
.n. '
DateL.h[ Rev. b4
. . - . _ , , _. .. .,. _ . . _ . _ _ . _ . . _ _ _ _ _ . . . _ . . - . . ~ , . . . . _ _ - - - .
- 1 l' . :
l
' X/Qs,x;= Relative average annual atmospheric dis-persion.for year of-interest at SITE BOUNDARY ,
,, in Sector *X (sec/m') '
l X/Qalr = Relative average ane al atmospheric dis-- , l- persion for year of interest at railroad, In-r formation Center. or Fricia Lock for distances ~ t
~'
listed below in Sector .'X(sec/m') ) Sector Distance to Location (m) l-Railroad Tracks: S. -
- 300 MW - D5 SW. 225-
'WSW: 225' W .225
'WNW . 345-NW' 450 ,
Information Center:- ESE- 884 Fricle Locic WSW- 450 0.25 = maximum occupancy factor for railroad tracks, Limerick Atomic Information Center or Fricks Lock Environmental Laboratory.(unitiess). 4.0 Radiological Environmental Monitoring Program L 4.1 Sampling Program The operational phase.of the' Radiological Environmental _ ! l 1: Monitoring Program-(REMP) is conducted in accordance with. l the requirements of ODCM 13.4-3. The objectives of the pro-- l: gram are: 1
- To provide data on measureable levels of radiation and radioactive: materials in the site environs i L
i P L Date M/PC Rev. N
. S, .
N ~' u 1'
. o .
d
- To evaluate the relationship between quantitles ,of
} ., radioactive materials released from LGS and resultant radiation doses to individuals from principal pathways .
' of exposure.
- I The sampling requirements (type of samples, collection fre- , ,
quency, and analysis) and sample locations are presented in Appendix B. 1 4.2 Interlaboratory Comparison Program a,
. Technical Specification 6.8.4.e.3 requires analyses be per-
. formed on~ radioactive material supplied as part of an Inter-laboratory Comparison.
Participation in an approved Interlaboratory Comparison Pro-p.1 provides a check on the preciseness of measurements-of radioactive materials in environmental samples. A summary j of the Interlaboratory Comparison Pi@.is results will be; i provided in the Annual Radiological Environmental Operating: ' I, Report pursuant to ODCM 13.5,'
- i
{ H.P. .> Date s 90 Rev.
,g, .
s e
'O F
s 9 1 4
5
. 4 o
4 4 M-4 4 n s 4
- D e
.0 s . ,
' e ,
9 .l i
= TABLES 4
0 : e e 1 e f 1
*?,
v e O s 0 0
. [s a
f g e f e 4 9 s e e t 9 ' J hI 4
,e i
e9 - 9 e
. e e ee * ' *
- L '* ' * * ' ' ' '* ' '* e .<= e' * *
- e * =
- e .o *e . .< *
- I
'l e
, s. ,
. s e:
.t
, ;i t
.: i
-I
. ,l 2.
sT*
< 4 s
e TABLE l~el'
. INGEST 10f' INDIVIDUAt. 00$E FACTORS (Daipj)
FOR LIQUID EFFLUENTS
'd r
< h t
i
,,~
'[,!
' UNITS FOR alt INGESTION PATHWAYS ARE:1 erer/pCl y Ll a
r ,e t i e 4
. . t ;
..e
+ ?
.S .
**4 a
e I s g e { t, 'j N s 4 9 O' g r t
.'k .
't t
t S 9 4 6
- 9. ..i t' f b
l i
+m, me , e -Is . ev e enem m e e m een em a o e ese.=ese i m ..e e ee o g g e se s om , iese o e,**eea e ..-e e e. . . .. , e see ,e e ,e e e s u '.'
.. - w *6- ,
- - - . . ~
. . < ' ?
LIJUI; .232 *a:73as. I I
'*t :
CA74.#2:A-714Li 2-1* :8 214. GJ:*111.1*1
- k & c 17 ' % *:st otCT:33.F38 aJuaft '
s
- 7. e::1 7418. ;0 f. ::n t f . LVN O!-LL!
. : * *. ! . L: vat
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.7134- J. 1.7 ! *7 4 113 4-;e 9 0 3- J6 se143 saa.; 4. 2 s i s- 47 1.*;;!
- C 1.J e:n-J! :.C J0 !* :C : .7 5t!-10 1.77Cir10 3.:v . 0
'. h&;42 1 16:f- J7 :.12:*-1C9 :.;6lf- M :.;**!*): 2. 3:1-00 0 0001-00 9.7701-05
. AUI3' s . a . w . ?l --i . 3 2 4. 1.17 * ! .1 0. C;0 3+0C C.C 01.J CC.C:Cl+
J,6 3:3-J3 0. 0 00!*3C 0016.614 1-06: f-0 5 3 1.12:1-05 6.C.;J-AC
~ 64161 7.17:;- 3 6. 3,; g.;g g.g3-g-;f . : g : 3. -
1 011*;
- ---4 s 1 3 -
14 C:-01 9.d;;f-Jt 1 14:1-44 0 03:2*00 2 36:1-05 0<000i+00 5.7J01-35 J:d*C0 4.7JC3-37 0.CC03-04 1.710t-34
- 2. ? s si- ;t 1.1:;j-Os .sts:-J7 0.
Ot:6-0.1 J 2 3- J J = J . ? '4 J- ; f 4.
- J C J- 18
.CJ0t*3C 1 1303-08 0.000l*00 6.*4Ct 4. 7 J0 2-0 6 PA1-J :.;30!.00 2.4 4 01-11 0. C 00!* 0 8L164
* .?':!**C 4. ;w C J-10 1 4101-1; C .C :C l* 0C 2.17 C 3-03 C.0 0 C !* 3 0 3. 600 !-0 5 J.' SCI-;)
a 14* 3.54*s-01 _f.:J:17 4..ig}- 3.es.2-30 7 J.1749-:7 C.C30det: C. 3:!*0C 0.00Cl* 00 3 6 40 3-0 5 1
- 147 1 11:r-Os 9.is:1-;: 3.61 l!-! C ' :.:0!*:0 2 0C0.00 la t: !*D:
1 93C!-07 0. 0 0 0 f
- 0 C . 2. 3 7 4 139 NJ44 :.C :04-0; C.JJ: 2 ;0 ;. 3:f.:: .. 00!*20
~
0.0:0!*00 0.0001-30
- . Sel.00 0.0301 00 C.200!-00 Nul :. :U* *: .C.C J01*'JC :.00C .:G .
e i a S
- e 9
4 s te' e k o e e h e
.f 9
G e e eemp . p __ --- er v
,, .g e
" = - ., ,
l 7 Table 1-2 Assiemptions used in I.lmerick Liqu_Id ' [ffluent Ikise Evaluation Descriptton .Value , Index 7.600E-01 l- Fractlen of produce from local garden 1.000Ee00
! Traction of leafy veg from local Iarden 2- 2.400E402 3- Soll: density in plow laver (kg/m* 2) 2'.500E ,
4- fraction of activity retained on sprayed vegetation 7.0000-01. s 5-- Shieldine factor Ior resIdertIal structures I.752Ee05
;; 6- - Period of buildup of activity in soll (br: ty (br) 7.200Ee02 7 --
Period of pasture grass exposure to activ I.440Ee03 8- Period of crop exposure to activity -(br) . 0.000E400'
~; Holding time in animal drinking water pond (hr J - 0.000E400-
' 9- Delay time f:.r Ingestion of grass by animals 10- s {hr) 2.160Ee03 l 11- Delay time for Ingestion of stored feed by an 2.400Ee01 i
12- Delay time for ingestion of-leaf veg by man (hr 1.440E403 13- Delay time for Ingestion of other weg by man (h ) ~ 4.8003e01
. Transport time milk-man ( i)consumption of meat animal (hr) 4.800Ee02 15-
~
ilme between sia ter a 7.000E-01 16- Grass yleid, wet t. g/m**2)- . 2.000Ee00-17- Other vegetation yle , wet ut Lkg/m**2) 2.100E-03 18- Weathering pale constant.for achtvity on vegetation (1/hr) 5.000Es01 19- Milk cow teed consumption rate (kg/ day wet) ~ 6.000Ee00 20- Goat' feed consumption rate (kg/ day wet . - 5.000Ee01 ~ 21-9eef cattle feed consumption rane kg/ ay wet) 6.000Ee01~ 22-Milk cow water consumption rat: (1 day) . .8.000E400 ~' 23-Goat water consumption rate (t/ day) 5.000Ee01 24- Beef cattle water conseemption rate 4 1/d 1.200E401 . Envt1 transit time for water Ingestion ) 2.400E401 25- Enytl' transit time for fish lagestion (hr l 2.400E401- . t 26 Enyti transit time for lavertebrate i sLion (br)' O.000Ee00
-l t
27 28- Enyt1 transit time ferishore exposure r)- * . 7;300Ee02' Water lagestion Ll/yr'i adeelt 5.100Eec2 { 29-30- Water ingestion Il yrll teen - 5.1000402. 31 - -Wateringestionll1yrschild
- y% _
n , ..._ _
; .. .~.- .r-8
. ._L. ______,__;_~____L-_ , _ _; _
- ~ . _ _ _ _ _ _ _ . _ _ . ~ -
=
. , ~ . :-. - - . _ -
A i
,,welEl-2(cent.)
~
I I~ Valse Description , Index 3.3000 02
. 1.200001 32-llater lagestles (1/yr? lefant 6.7000 0t Shore exposare fhr/yr; adwit 1.4000 01 33- Shore exposare Lhr/yr < teen 0.000 0 00-34- Shore exposare ' br/yr ichild 2.100 0 01 35- -
Shore exposare Chr/yr i lefant 1.6000 01 36- Fresh water sport fish lagentlea Lt yr yr?' teen adult 6.3000 00 31- Fresh water sport fisk fagestion Lt t yri child e.co000r 38- Fresh wter sport fish lagestles L g lefant 39- 2.100 0 - kg 40- Fresh water sport fisk fageestion kg/yr ' teenIFresh water commercial 1.6000 (i 6.g000 00 fish lagest los/p 41- - Fresh water commercial fish lagestion ILtg/yr' child 42- e.eeoboo 5.0000 00 43- Fresh water commercial fish k lagestleaFresh yr? adult water commercial3.8000 00 fish Ingestles ikg/ 44- Fresh water levertebrate lagestlen I 'It yr . teen I.7000 00 45- Fresh water levertebrate Ingestion k yr. child e.000000 46- Fresh water levertebrate lagestien k yri lefant 2.100 0 81 41- fresh water invertebrate Ingestles /yr[ adely 1.6000 01 4 48- Salt water sport fish lagestles ikg yr teen -6.9000 00 49- Salt water sport tid lagestion 'k6 yr ' child t 58- e.000000 Salt water sport fish lagestlen t yr ) lefant 2.100 0 81 51- 1.600 0 01
- 52- Salt water sport fish lagestiesSalt kg/yr water
. teen commercial fish lagestion 6.9000 00 ilig/yr? adult-
; 53- Salt water c y mercial fish lagestles i bg/yr ! chlid e.000000 1
; 54- Salt water comm<'rcial fish lagestles - kg/yrl lefant 5.00000s
} - 55- Salt water commercial fish lagestles 3.8000 06 . 3 ' ; 56- Salt water levertebrate -Ingestles (kg/yr? adult 1.700 0 00 5F- Salt water levertebrate lagestlee ykg/ 6 yr yrs teen child - e.secoce
- 58- -SaltwaterInvertebratelagestles( i lefant 6.F90el
}
53- Salt water levertebrate lagestion qt yrl adult 4.2300 01 j 60- Irrl ated leafy vegetable sagestlem 1 'k yre teen 2.6WAsel
- 61-Irri ted leafy vegetable lagestles ' & yr. child 0.0000 00
' 62- Irri ted leafy vegetable lagestien t yr lefant ,
5.2000 e2. 63 Irrt sted leafy vegetal =!e lagestlen I k pr? adult
- 6.300Ee02 ted other vegetable ingestion 64- yr. teen 5.2000 02 65- Irri sted elleer vegetable lagestlen Lt& yrc child Irrl e.060000 66- Irri ated alleer vegetable lagestlen.ltg/yr) lefant 67- Irrigated other vegetable lagestion 68- .
. . .4 .-*** - ~ . _ _ _ __
g
. ;}TAntEl-2(cont.) .- -
, --= _
l
'Inden Description . Value -
69- /yr,adalt prrigated root vegetaMe Ingestlen 5.200002 llkg ' kg/yr;' teen 74- Irrigated resa vegetable Ingestion 6.3000 02
~
. 71- ~
Irrteates reet vegetaMe Ingestion ikg/yrl child 5.200002 [ 72- Irrlijated root vegetable Ingestion ikg/yri infant - 0:000000 73- Irri sted cow mil'k ingestion '1/ yrs adult' 3.100002 i 74- 1-ri ated tow al' A Ingest ha 4 1/yr teen
. t 4.0000 02 75- 'rrt sted cow y'afk IngestLa i I/yry child
' 3.300D 02 76- Irrigt,! -, milk Ingestion I,l/yr i infant 3.300002 77- 8t>rigated goat milk ingestion 11/yr? adult 1.100D 02 78- Irrigated goa6 Milk lagestion i 1/yr) teen i 4.0000 02 !
73- Irrigated get allk ingestion i I/yry child 3.3000 02 !
- 80- - frri Infant 3.300D 02 80- Irri etedtedbeef goatIngestion milk ingestion Th yryi;1/yr)lt adu 1.100D02 i
42- Irrl ated beef ingestles i k yry teen 6.5000 01 i . 83- ' Irrigated beef Ingestien Lk yry child 4.1000 Cl j . 94- Irrigated beaf lagestion ' kg/yr? Infant 0.0000 00
- 2 3
e t l * ( - . I s 1 ' i i 1 * - 1 b - l i
- i 1 . .
i y i 1 l ' ] i l I 1 i i ( .
l Tt.BLE 2-1
l DOSE FACTORS FOR NOBLE GASES ;
< -i Total Body Beta Skin Gamma Air Beta Air l Dose Factor Dose Factor Dose Factor- Dose Facto' Ki (mrem /yr (mrem /yr M1 (mrad /yr Ni (mrad /yl Inddx Radionuclide pCi/m Pej
) pC1 j) pCi j) Per pCi/m 3)
]
-3 Ar 8.84E-03 2.69E-03 9.30E-03 3.28E-03 4 Kr-83m 7.56E-08 --------
1.93E-05 2.88E-04 5 Kr-85m 1.17E-03 '1.46E-03 1.23E-03 1.97E-03 6 Kr-85 1.61E-05. 1.34E-03 1.72E-05 1.95E-03 7 Kr-87 5.92E-03 9.73E-03 6.17E-03 1.03E-02. 8 Kr-88 1.47E-02 2.37E l'.52E-02 2.93E-03 9 Kr-89 1.66E-02 1.01E-02 '1.73E-02 1.06E-02 10 Kr-90 1.56E-02 7.29E-03 1.63E-02 7.83E-03 11 Xe-131m 9.15E-05 4.76E-04 '1.56E-04 1.11E-03 12 Xe-133m 2.51E-04 9.94E-04 3.27E-04 1.48E-03 13 Xe-133 2.94E-04 3.06E 3.35E-04 1.05E-03 14 Xe-135m 3.12E-03 7.11E-04 .3.36E-03 7.39E-04 15 -Xe-135 1.81E-03 1.86E-03' 1.92E-03 2.46E-03 16 Xe-137 1.42E-03 1.22E-02 '1.51E-03 1.27E-02' 17 Xe-138 - 8.83E-03 4.13E-03 9.21E '4.75E-03= 1, l t 1 6 .
. .. . _ . . ~ . . _ . . ~ = - . . _ _ . -. . - . _
TABLE 2-2 l . k INDIVIDUAL DOSE FACTORS (DFFOR GASEOUS EFFLUE l UNITS FOR AIRBORNE PATHWAYS
- (PATHWAY NUMBERS 1 AND 7) ARE
- ;
3 mrem m /Ci sec , [ UNITS FOR DEPOSITION PATHWAYS i (PATHWAY NUMBERS 2 6) ARE: l 2
- mrem m /Ci ,
i
. l J
i i Pathway No. Pathway . I' P1we l 2 Ground . 3 Vegetable - 4 Heat 5 Cow Milk 6 Goat Milk *
- 7 Inhalation l
l I k S s i e a. N g , y 4
.. ..... . . ....- :.. . . . . . .....~. _... .. . . - . - ~ ._. . .. . -
* = - .- v - - - , , - - . , . - - -
#.. .,-m-. .* --~- .e- - - - -- - -- , - - ,-- m...--,
N
- l i 1 IN0!VIOUAL 00$! FACTOR $ FCR
..... . ........ ...... .. .....G A
- 10U $ ! F...................................
.8 L U 1 N Y 3 -- F O R I S G T O P E : H3 ... f I-
' r0R PATHWAY: P.UME T. BODY GI-T4ACT EON! LIVIR K10N!Y THYROIO
- ADUlf:
TE*K: 0.0;f+00 0.004+00 0.0 0! + 0 p 3.0 0:+ 0 0 0.000+0p 0 30i+ 0 0 0.00E LON3 + 00 0 00E+00 SKIN 3 CM!LO: 0.0)i+00 0.J0J+)C 0.00i+09 3.3 0.000 00 0.00c+20 0.00E+00
- 0. )* 00 0.00*
j 2NFANT: C . g J ! ++ 0 0 0.00f+30 0.0Jt*0J 3.06':+00:+00 0.00C+03 0 00!+ 00 0.00& +00 0 00!* 00 0 004+00 0 00:+ 00 0.00E +00 0.00t+00 ,j 0.00t+90 0.00E+000. J 000! 1 FOR PATHWAY: Ot0UNO ADULT: T. 600Y GI-TRACT $0h1 LIV!A K: DNtY T A Y RO ID' L U N'G $ KIN I 0.0)f*00 0. TE!N: 0 03E+00 0. Q 0 8+ 30000 J0!+00 0. 0 0!+ 00 03.30!+00 0 3.C J 8+ 0 0 0 0.0 0 E + 0 0 0. 00!+ 0 0 0.00 E + 00 0.0 00E+00 CHILO: 0.0Jf+00 0 00'+00 0.00g+00 .+ 0 008+00 0.00E+00 0.30'+00 0.00f+0'3.00J+00 0 00E+00 0.00 INFAN7: O. 0 0 2+ 0 0 ' 0 03t+00 0.00 3+ 00 0.0 0E +00 0.00!+ 00 0 00E +00 0.00!* 00 0.00E + 03 0. 00!+ 00 FOR PATHWAY: V!G 5T A6Li-AOULT: T. 200) GI-TRACT BONE LIVER KICNEY THYt010 1, U N 3 SKIN' t TEEN: 6.53:+01 6.333+01 0. 0 0i + 0 0 5. 5 3 + 31 6.53E+01 6.53!+31 6.531+01 0.00 +00 7.734+01 7. 1 1.21,+021.!158+01 0.00 +00 CHILO: 7.T5U + 0! 0 00 +00' 0 0 3 + 0 0 0 0 02-0.00}+00 1.21f.75+ +01 7.75E+01 7.758+0 I t INFANT: . 0 3 ++ 0 0 0. 0 0 0d0.0$e+00
- 0 0 0. 0.00!+ 3 0 +30 3'0200E.00
- 1. 2 ' 0. E 00a+00
+021 t
l l FCR PATHWAY: M! A T T. 30DY GI-T4A;T EON! ' LIV!R ADULT TiiN: 7.9)!+03 7. 7 3 2+0 0 0 0 0!+0 3 7. 9 8 5+;0 7.9 KIDNEY 3E* 0J 7.T4YR0!D . LUNG 9 E:+ 0 c 7.94 E +00 0. 30 E+ 00
- $ KIN
- CM*LO: 5.75!+00 5.T 4.75E+004.7!i+00000{+00!+ 0 0 0. 05.75E*00,5.75f+00 0 +0 0 4.76 4+ 5.75E+00 34. 07eE4.7
+ 00a0.40 0+E0+ 0 ) 04.
0.03s+00 0.00!+00 0 00i+00 ~.755+00 0.00E+00 ZNFANT2
. J0!+ 00 0. 00E+00 0. 00i+ 00 0. 00E + 00 0. 00d + 00 FOR PATHJAY: C3W MILK '
ULT: T. 6 00Y GI-TRACT BON 3 liv!R K'ON&Y THYRCIO LUNG
- 1. SKIN
, .4N: 2.6 83 3E +E01+ 01 J.3SJ+J1 0.00E+00 1.3SJ+31
- 2. 4 5 3+ 31 0.00!+00 1.458 01 . 43l+01 {.398+01 1.iJi+J1 1.33E+01 0.00!+00 -
CM LO: 3.87*+01 3. 78 . 4 5 f + 01 2. 4 5 E
- 01 0 00!+00 I N E' A N T ! 5.81!+01 5. 73++31 0.0*E+00 3.375++01 S 0.00* 00 '
31 0 061+00 5.372+01 3 878+E^l37!+ 1 3 47!+01 5.J71+01 3.87E+01 3.87E+01
- 0. 0 0 ! ++ 0 0 FCR PATHWAY: G3AT MILK A 0 UL T:
T. 8 0DY GI-T R ACT 10NE LIV!R KIONEY TMNROID UNG SKIN < TEEN: 3.835+01 4 3.32i+01 0.00E+00 9)E+01 4.998+01 0.00E+00 3.83f+01 4.198 3.83E+01 3.33E+01 3.83(.+01 0.00!+00
- CHILD: 7 8)!+01 7.39:,*01 0.00!+00 7.89!++01 4.99E+01.*.99E+01 4.99E+01 0.00!+00 INFANT: 01 7.89Ev01 7.395+01 7.59E+01 0.00f+00 L 1.23 2 + 02 1 2 0!+ 02 0. 0 0!+00 1 2 0E+ 02 1.2 0$ + 02 1 20!+ 02 1.20E +02 0. 00i+ 0 FOR PATHWAY: 11HALATION ADULT: T. SODY GI-TAACT EONE LIV!R KIDNEY THYROIO.
4.01E+01 4.01!+01 0.00E+00 4.015+01 4. 015 + 01 4. 015 + 01 4. 01LUNG SKIN TE!N: E + 01 0.00!+00 CHILO:
- 4. 0 5 E + 01 3.57E+01 4.03f+01 3.575+01 0.00E+003.57E+01 0.00E+00 4.33&+013.57E+01 4.03E+0134.0 5 3+01 4 03E+01 0.00E+00 INFANT:
- 01 3.57E+01 2.05E+01 2.055+01 0.00E+00 2.05f+01 2.05E+01 2.0 3+01 + 2.0$E+01 00.00!+00 00i+00 ,
i i i e t
)
i I b 4 (. i AA =
- k
)
TNDIVIDUAL D353 FA TORS FOR G13!003 f F.8 LUE17 3 -- F OR 2 3 073P E
- C14 I eCR PATHWAY! P .UME 8
T. 830Y GI-T4ACT AOULT: 0.03&+0 0.308 00 BONS L!V!R K!CNEf TkYROID LUNG 1 KIN
.. TE8Nt 0. 0 3 E + C, g 0 00d+30 0.00E+00 0.00!+00
! CM!L32 IhPANT!
0.03E+C0 0 0.000 +00 0 } 0.00.
++ 3030 0.. 0j 0JO] c.00E+00 0.0]E*00 0.30.l+000.00E+00g.5'Q++000.00E+000.gC+000.00e+00
++ 0 3 0. $ i + 0.00E*00
- 0. 00*00 0 0 0 00.00 0 e+00 0.30!+00 + 0 J: ;
0.00e+00
- .FCR P A T M d,A Y 2 G100ND T. B30Y G -7.s;7 LIVdR KID:lfi AOULTL $CN8 T h Y R O I D' '
LUWG $ KIN TE*N! 0 0)E +0 3 3. 0.0JE+00 0. 3' f8+00 30 0.0 0E
- 03 0. 00!+ 00 0.00l+ 00 0. 00!+ 00 0 00E + 00 0.30f+00 CHfLDS 0 03E*00 0..y J!+30 0.0 0f +03 0 008+ 00 0.00!+ 0g 0.00!+ 00 0.00E +00 0. 0 0!+ 0 0 0.00E+00 ,
INFANT: 0.00l+30 0.00!+0. 0 03 E + 0 0 0. 0 0 !+ 00 0. 0 0!+ 00 3. 002+ 00 0. 0 0 E+ 0 3 0. 0 01+0.00!+00 0 0 0. 00 E i POR PATHWAY 1 V!GJTABLE T. 300Y GI-Tta;T BDNE LIV!R KION!f ADULT! 5.23E+03 5.
- T.4Y 2 0 ID LUNG $ KIN Tf!N2 CHIL31 8.7fE+03 8.j25+33 .15+33 2.615+0+ 5.221+03 5 2'E+0333 8.7 I +
3.75E+ 03 5. 22 5 + 0g 5.T'2 E + 03 0.0 0
*4 06 4.b'9E+04
- 1. 7* 3.798 2 143+?. B.
3 INFANT!, 0.03f+00 0. 2 +30!'+00 0.00l++05 2.143++040 0 3. 00!+ 2 14* 04 J4 0.00i+00 POR PATHWAY 2.1*f+0+ MEAT 0.00!+00 0 0 0. T. 500Y GI-74A;T $0N2 L* KICNEY ADULT: 1. 6 4 E + 0 3 THYRDIO LUNG $ KIN TE N3 1. 64 3 + 33 8 22E + 03 1. s 4.I03+V1.6+E+03 !R 1.44!+0S 1.64E+03 0.30!+00 t OM LD* 1. 3 ) E + 0 3 1 398 2 IN ANT 2.61E+03 2.21}++ 3 6.965+03 1 31g+0+12.613+03 298+03 1.39E+0g2.01E+0. . 11:+ 2.612+0303 1.3st+03
}.394+03 0.00a+
0.03E+0J 0.00!+ 0.00!+00 POR PATHWAY 0 0.00E+00 0.00E+00 0.00E+03 0.00E+00 0.00E+00 0.00!+00 C3W MILK JULT: T. B30Y GI-T4ACT 13N! LIYiR KIONEY TMYROID LUNG SKIN
.ifN8 1.795+03 1.7ti+33 3.97E+03 1. 7 9 5 + 0 3 1. 7 6 5+ 03 1. 7 9 5+ 03 1.7 9 E + 03 0.002 3' CMIL32 3.31 E + 0 3 3. 315 + 0 3 1.6!!+04 3.31d+03 3.31E+03 3.312+03 3 31E+03 0.00!+00 8.13*
INFANT! 1.73E++03 5.125+03 4.075+04 8.13E+03 E.1JE+03 $.13?+03 8.13E+03 0.00!+00 FOR PATHWAY 04 1 70!+04 7.975+04 1. 7 0 !+ 0' 1. 7 0 !+ 04 1.70!+06 1.70!+04 0 00!+00 4 G3AT MILK c ADULT! T. BODY G -TRA T BONE LIV!R KIDNEY TMYROID 1.7 7 E + 0 3 LUN3 SKIN TEINt 1. 7 9 3+ 03 s. 37 E + 03 1. 7 91+ 03 1.T 9E+ 0 3 1. 7 9 ?+ 03 1.7 9 50.+0 0y 0!+ 0 0 CHIL32 3.31E+03 8.13 E +03 3. 3.312+03 la f + 0 3 1 65E+04 3.31E+0) }.31E+03 3.31c+03 3 312+0. 0.00i+00 INFANT 4. 0 71+ 0 4 8 135+03 s.13 E+ 0 3 3.13 *+ 03 8.13 E + 03 0.00!+00 1.73E+04 1.7Ci+04 T.975+0+ 1.70!+04 1.73E+04 1.703+04 1.70E+04 0.00!+00 < FCR PATHWAY 3 INHALATION 1 AOULTt T. 600Y GI-TtACT 60N! LIV!R KIDNEY THYROIO LUNG - l T!!N8 1.
- 1. 50!E 4 E+0
+ 2 0 2121 0 3 40 2 3 + +02 0 2 5.7 6E 6.2*E+02+ 02 1.
1.54E+02 082+ 02 1.54E+02 1.0 8 6+ 02 1. 04 E+ 02 1 03 E + 0 2 0. 0 CHILDS 2.13E+L , INFANT: 2 13 !+ 0 2 1.14 E + 0 3 2.13 f + 0 2 2 13 E + 0 2 2.13 3 + 0 20.00: 2.13 E00+ 021 1 65 E + 02 1. 6 61+ 02 8 3 9 6+ 0 2 1. 64 E+ 02 1.6 5 E+ 02 1.4 4 5 + 0 2 1.6 4 E +02 0. i l 1
.)
- 3. +. . . A J ~ 1... ..J. ...i.d :.s ,......"..... 1. e.'.L....E.-.- ~. .J G a ss 4 . i
. l l
l
'NDIVIDU.L 00$! FA; TOR $'.80R 3A$EDU$ dFFLUENTS -- FOR ISOTOPl AR41 i FCR PATH 4AY: P.UME ,
I T. SODY GI-TRACT EON 8 LIVfR KIONEY THYR 0ED - LU
*. AD 6+
1.,$,1.02 0' 1.9 E+02 1.963+5z 1.965.N3 3.2 $ KIN
., InULit N! 1., 02 2.16!.+02
- 2. ,6 : 0: 1.968 :.2A 02, 1.?,ti1. A 2.> 2.,.,!.0z 02 02
. 4+02 2.2,1 0 5 1. er.01 1.,AE.02.,*E.02 .> 1. E+ 113+.a2
.: 0:
q IN; ANT! tot 1. 0
- 1. ,,,, g .+ 0 32.2 . 0,6 3 + a t 2..g.005 1.i,64 02 02 1. .E+0: 2. 63.+52 1
+c3 2.,,e.0202 3 1.;++02! .
PCR PATHWAYt Gt0VN3 , j T. B ODY GI-TRACT %CN! LIViR KIONEY THYROIO LUkG $ KIN ADULT! 0. 03 E + 0 0 0. 3 0 !+ 0 0 0.00E+00 0.00 3^ 0.00f+00 0.00!*00 0.00E*00 0.00 +00] TEEN! CMILD1 0.03f+00
- 0. 0 3 E 0.00$
4 0 0 0. 0 0 }+ 0 0 0. O N E 1.00!+0J .0 0 0. 0 0.0.j0 0!+0 ++ 00 0. 00E+ 00 - 0. 0 0 + 00
+00 0. 0 6 6 + 00 D. J 0 !+ 0 0 0.0 0!+ 0 0 0. 0 0 !+ 0 0 0. 0 3 E + 0 0 0. 0 0 + 0 0 1
INFANTt 0.03E+00 0.00!+00 0.00E.00 0.30!+00 0.00E+00 0.00!+00 0.00E+00 0.00f+00,
. FOR PATHWAY V!GETAELE ;
T. BODY GI-TRACT $0N! LIV!R KIDNEI THYROID LUN3 $KINi ADULTt 0 03E+00 0.00f*00 0.00!*03 0.00E+0* 0.00E+00 0.00!+30 0 00E+00 0.00* 0l+
- 0. 0 0!+ 0 g 0 0 0 + 0 8 0. 0 0 E + 0 3 0. 0 0!+ 0 0 0. 00 8 + 0 0 0. 000!
TEEN CHIL31 0.0)E+00 9 30 +00 0 0Ji+00 0.J0 +30 0.00*+0g 3.00 + 00 0.00E +00 0.00!+ 30 0.00l+00 0.003+ 00, INFANTt, 0.03d+00 0.30 *00 0.00E+0J 3.00 +00 0.00E+00 0.00!+00 0.00E+00 0.00!+00! FCR PATHWAft M!AT T. BODY GI-74ACT BONS LIV!R KICNEY TMY10!D LUN3 $KINi AD LTt 0.03!+00 0.00 +30 0.00!+00 00 TE N 0.3JE+00 0.30 +30 0.00!+00 0.00 +00 5 000.00E.+00 0,003 0.00 0.00+00+000.00 00,+00 0 E + 00. 0 0. 0 0 0+ +00 00 CH LO! 0.03E+00 0.00 +00 0.00!+00 0.00E+00 0.00l+00 0.00 +00 0.00E+00 0. 0 0 + 0 0 : INFANTt 0.032+00 0.301+30 0.00E+00 3.00E+00 0.00t+00 0.00!+00 0.00E+00 0. 00!+ 0 0 : FOR PATHWAY C3W MILK T. 800Y GI-TtACT ! NE L VER K'DNEY THYRCID LUN3 $ KIN
.DULT! 0.0]E+00 0.30f+00 0.03E+00 0.00!+00 0.05E+00 0.00s+00; lAl"it INFANT!
8:831*888:!S!:888:88!:8!8:!8i:o88:881:88'S.00s+000.00E+ 0.03E+00 0.00i+00 0.00!+00 0.00!+ 0 0.00E+00-0. 0!+00.00E+000.00!+80' O: 8!:
. FOR PATHWAYt G3AT MILK t T. 800Y GI-TRACT BONE LIY!R KIDNEY THYROID LUN" SKIN' ACULTt 0.03E +00 0.30E+00 0.00E+00 0.00!+ 00 0.00E*00 0. 00!+ 00 0.00E & 36 0.00E+00' TEEN 0.03E+00 0.00!+00 0.0 0E +0 0 0.0 0E+ 00 0.0 0E+ 00 0 00!+ 00 0.00E +00 0 00E+00:
CHILD 0.03 E +00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.003+00 0.00E+00 0.00E+00 INPANT! 0.03E+00 0.00i+00 0.00l+00 U.00!+00 0.00E+00 0 00E+00 0.00E+00 0.00E+00' FOR PATHWAft I1MALATICM T. 80DY GI-TRACT BONE LIV!A KIONEY' THYROID LUN3 $ KIN ADULTI 0.03E+ 0.00!+ 00 0. 00E +00 0.0 0s+ 00 0.00E +00 .00E+00 0.00 +00 0.008 TEEN! 0.03f+00 00 0.00f+00 0.00t+00 0.00!+00 0.00E+00 .00* +00 CHILDI INPANTt 0 93E+00 0.00* 0 0 0 E + 0 0 0. 0 0 E+ 0 0 0.0 0E+ 00 0. 0 0.w3E+00 0. 0 0 l++ 0 000 0.00E+00 0 00E+00 0.00E+00 0 00d+00 0.00E+00 0. 0 0!+ 00 0 00 +00 0.00f+00 l ; l
. .cm_ - - , . . . . , . _ _ . . _ , , _ . . . , , . . , ,,,
~~ ~ ^ ^ ^
C . C
~
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* ?NDIVIOUAL 00$! FA070K$ FOR JASEOUS EPPLUENT3 -- POR ISOT081 : KRS3M FOR PATHWAY: P.UME l i
4 ADULT: T. BODY GI-TRACT BON! LIV!R K I O.1 E i THYR 020 TE8h: 1.65E-03 1.5Ej-03 1.6 9 5-03 1 6 3g LUNG SAIN
, CHILO: 1.636-0* 1.664-33 1.6 !-03 1.o6.-003 3 1.68E-03 1.d4E- 1 1 683-03 064-03 9 398-02 4.752-01 1 6.g{-03 1.ng!-03 1.e53 v@J 1.663-03 9. 1E-02 4.7 g 01 1 65'- 9.
INFANT: 1.cl! 0! 031.6t!-O' 1.bd!-05 1.6St-03 1. b o i- 0 3 1. 6 8 4-30 3 1 666-03 9. 9E-02 7E-02 4.7 . 01 4 7 !-01 FOR PATHWAY: G40UND ,
, AOULT:
- T. 500Y GI-TRA T SON! LIV!R KION!Y fnYRDI6 LUNG 0.031*00 0.00!+ 00 0. 00!+00 0.bO3 + 00 0.00!+ 00 0.0 8 00 0.00!+00 $ KIN T!EN: i CMILO:
INFANT: 003!++00 0.00!+00 0. 0 0 E + 0 0 0. 0 0i + 0 0 ' 0. 0 0E + 0 0 0. 0 !++ 00 0. 0 0E + 00.00!+00 0.00 0 0.00!+00 0 0 3 E *000 00.00$ 00 00.00E+00
- 0. 0 0 !++ 0 0 00$+00 2 0.00!+00 0.0 !+00 0.00E+00 0.00* 00 0 00f+00 0.00.+00 0.00E+00 0.00!+30 0.00E+00 0.00!++00 POR PATHWAY: V! GETABLE A0 ULT: T.'600Y GI-TIA07 CONE LIV!R KIONEY THYRCIO LU SKIN
'TE8N: 0.03E+00 0 00 +00 0.00E.00 0.00*+00 0.00E+0J 0.00!+00 0.00$+NG 00 0.00!+00 Ch!LO: 0.03E+0C 0.00 +00 0. 0 0 E + 0 0 0.0 0!+ 00 0. 00f
- 00 0.00!+30 0.00!+00 0.00* 00 l INFANT 0. 03 E
- 00 0.30 +00 0.00E+00 3. 0 0!+ 0 0 0. 0 0!+ 0 0 0. 0 0!+ 0 0 0. 00E + 00 0.00!++00 0 0J E *0 0 0.0 0!+0 0 0. 0 0E+ 0 0 0. 0 0!+ 0 0 0 03E+00 0. 00!+ 00 0 00E + 0 0 0. 00E+ 00 FOR PATHWAY! M!AT A0 LT: T. 800Y GI-T.1 A0T SONE LIV!R KIONEY THY 10IO LUNG TEyN: SKIN CHILD:
0.03!+00 0.00!+00 0. 0 0 E + 0 0 0. 0 0i+ 0 0 ' 0. 0 0!+ 0 0 0.00!+00 0.00E+00 0.00!+00 0.0)E+00
- 0. 3 0 E+ 00 0. 0 0!+ 00 0. 00!+ 00 0.00E+00 0.00!+00 0.00E+00 0.00!+00 INFANT: 0.00E+00
- 0. 00! + 0 0 0 00i+JO 0.0 0E +0 0 0.00d+ 00 0.00E +00 0.00!+00 0.00E+00 0 00!+00
- 0. 00 t+ 0 0 0 0 0E+ 00 0. 00!+ 0 0 0.00i+ 00 0. 00!+00 0.00E+ 00 0. 00!+00 FOR PATHWAY: C0h MILA AULT: T. 5 00Y GI-T R AIT SON! LIVER KIONEY TMYR'ID LUNG 3 KIN
.EiN:
CHILD: 0.00E+00 0.000+00 0.00E+00 0.00!+00 0.00E+00 0.00!+00 0.00E+00 0. 00!+ 0 0 INFANT: 0.03E+00 0.03E+000.00 0.00*!++00 0.00E+00 0. 0 0!+ 0 0 0.0 0 E + 00 0.00i+00 0.00E+00 0.00! " 00 0.00E+00 0.30E+00 0.00E+00 0.00i+00 0.00E+00 0.00!+00 0.
, FOR PATHWAY: G3AT MILK 03 E + 0 0 0.00!+00 0.00E+00 0.00!+00 0.00f+00 0.00!+00 0.00E+00 0.00!+00 , ADULT: T. 600Y GI-TRACT SONE LIVER KIONEY THYROIO LUNG SKIN TEEN: 0.03 E
- 0 0 0.00!+ 0 0 0. 00 E+00 0.C SE+ 0 0 0.00E+00 0.0 0!+ 00 0.00E + 0.
0.03E+00 000 0!+ 0 0 CHILD: INFANT: 0.00E+00 0.004+00 0.00E+00 g.00E+00 0 00E+00 0.00!+00 0.00E+00 0.00!+00 0.00: +00 0.00E+00 v.00i+00 0.00E+00 0.00! +00 0 00!+00 0.0 0i+0 0 0.00!+ 0 0 0.00E+00 0.00!+ 00 0 00E + 00 0 0 FOR PATHWAY: 11HAL4 TION AOULT: T. S C0Y GI-TRACT BONE LIVER KIONEY TdVRDID LUNG $ KIN l TEEN: CHILD: INFANT: 0 0J E + 0 0 0.0 0!+0 0 0.0 0E+ 0 0 0.00 e+ 00 0.0 0.03E+00 0.00* 00 0.00E+00 0.00* 00 0.00 +00 0.00S 0 +0 0 0.00i+00 s
- 0. 03E + 0 0 0. 0 0 !++ 0 0 0. 0 0 E+ 0 0 0.0 0!+ 0 0+00 + 0. 00.00E+00 0 E + 0 0.00i+00 0 0. 0 0!+ 0 l il -
'1 j
h se .
)
^
- . .. . .T . . . .... . .. -.. . .....~ ..:..~.T. .n.. . . . .: . : - :.:.
i + 1 H 1
; INCIVIOUAL
.............. 00$!'. FACT 3RS 7CR GA3E305 277LJE4T3 -- F3R I$070PE
- KR85 est PATHWAY 3 P'. UME T. BODY GI.TtACT SONE LIVER KICHEY THYRD
,, ULT! . 5 7 E -01 3.$7!-J1 .57E-01 3.575-01 . 7E-01 3.371bO' LUNJ 4.29fKIN 1 9.50E-01 +01 N2 .515-0 J.57 -01 .!7E-01 3.375-01 . 7E-01 .
d- 1 ?.501-0 4 29!+01 CM L32 3.57E-0 3.57.-01 3.57E-01 3.$75-01 1 9 50!-0 4.29f+01 INFANT! 3 51E-01 3.571.01 3 57E-01 3. 3. f75-01 T I-013 5TE-01 3.I !
.375-01 9 502-01 4.29E+01 FOR PATHWAY 2 GROUNO i .
ADULT! 0.T.03E 800Y+ 00GI-TRACT
- 0. 3 0 + 0 0 0. 0 0! $CNE
+ 0 0 3.3LIV!t 0!+ 0 0 0.0 KI 0g+00 NEY 0.THYROTC 00i+ 0 0 0. 00tLUND $ KIN
+ 00 0.00!+00 "
TE8Nt 0.03*+00 0.30 +00 0.00E+00 3.00!+30 0.00E+00 0.00!+00 0.00E+00 0.00 CHILD 0. 3 E + 0 0 0. 0 0 + 0 0 0. 0 0 E + 0 0 0. 3 0i+ 0 0 0. 0 0 + 0 0 3. 0 0 f + 0 0 0. 00i + 00 0 0 0.; , INFANT! 0. 3 E + 0 0 ~ 0. 0 0 !+ 0 0 0. 0 0 E + 0 0 0. 0 0 E+ 3 0 0. 3 0 + 0 3 0. 00!+ 00 0.00! +0 0 0 00!+ 00 . POR PATW.2ft V!G E T14 LE 7.'600Y GI.TtACT &DNE LIY3R KION!Y THYRDID 1.JN3 $ KIN A 01 T t l'. 03 E + 0 0 0. 0 0 !+ 3 0 0.0 0 5+0 0 3.00!+30 0.032-00 0.30E+30 0.00 i+ 0 0.00E+00 T fN 1.0 3E + 00 0.00 + 00 0.00E+00 0. 0!+00 0.00E+00 0.00f+00 0.00H+ 0 0. 00!+ 30 . CHILD 2 s.03f+C0 0.30 +00 0.00E+03 0. Di+30 0.00 0 3 0. 0 0!* 0 0 0. 0 0l+ 0 0.00!+00 INFANT! , J.03E+00 0.00!+00 0.00E+00 0.00!+00 0.00{++00 c 0.00!+00 0 00E+00 0. 0 0!+ 0 0 POR PATHWAY 3 MEAT T. 800Y 3I-TRACT 53N! LIV 3R KICN!Y THYROID LUNG SKIN ' 4 AO LT! Nt 0.0)E+00 0.00 +30 0.0gl+00 0.00 +00 0.00E+00 0.00!*00 0.00E+00 0.00 +00 0.00E+0 0.30 +00 0.0.1+00 3.00 +00 0.00E+00 0.00i+00 0.00$+00 0.00 + 00 - ' LO: 0 03E+0 0.30 +00 0.000+00 3.00:+00 0.00&+00 0.00f+00 0.00!+00 0.00 +00 INFANT! 0.03E+00 0.002+00 0.00E+00 0.00!+00 0.00E+00 0 00!+00 0 00E+00 0.00!+00 ' PCR PATHWAY C3W MILK T. 630Y GI-TRACT SONE LIV!R KICN!f THYROIO LUNG 0.0JE+00 0.00!+30 0.00E+00 3.00!+00 0.00E*00 0.00!+00 0.00f+00 3.00gKIN JLT! .+00
.iN CHIL32 0.03t+00 0.30f+30 0.00E+00 0.00f+00 0.00E+00 0.002+00 0 00E+00 0.00!+00 0.0Je+00 0.00!+00 0.00E+00 0 00!+ 00 0.0 3E + 03 0.00!+ 00 0.00E + 00 0. 0 0i+ 0 0 -
INFANT! 0.03E+00 0.00i+00 0 00!+00 0.00f+00 0.00!*C0 0.003+00 0.00!+00 0.00!+00 F3R PATHWAY G3AT MILK . l l
, ADULT!
T. B ODY GI-TRACT SDNf LIVER KIONEY THYROIC LUNG SKIN 0.03E+00 0.00!+00 0.00E+00 0. 0 0!+ 0 0.00E+00 0.00!+00 0. OE+00 0.00!+00 T!!N 0.03E+00 0. 0 0 i+ 0 0 0.00E+00 0.00E+0 0.00E+00 0 00!+ 00 0. OE +00 0.00!+00 CHIL32 0. 03 E + 00 0. 3 0 *+ 0 0 0.00E*00 0.00i+00 0.00i+00 0.00E+00 0.00E+00 0.00 +.00 INFANT! 0 03E+00 0.00$+00 0.00E+00 0.00!+00 0.00E+00 0.00!+00 0.004+00 0.00 +00 FOR PATHWAft I1H AL ATION . T. BODY GI-TRACT L VER KhDNEY 0.0 THYt010 SKIN AOULT! 0.0)E+ 00 0.00!+ 0 0 0.00 4SONE +00 0.0 0j+ - 00 0.00R+00. 03+ 00 0.00E+ LUNG 00 0.005+00 TEEN CHILD: 0.03E+00 0.03E+00 0.00!+00 0.00!+000.00H+00 0 00 H+00 0.00g++00 00 0.00R+00
- 0. 0 00*l+00 .00E+00 00E+00 0.00!+00 0.00E+00 INFANTt 0.09 0.03E +00 0 00i+ 00 0.0 0 i+00 0 0v1+ 00 0.00u+00 00 WOO0.00 + 0g .00E+00 0.00E+00 0.00!.+0v l
l . k
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' +
I INDIVIDUAL DD5! PACT'R$ FOR GA323US JP8LUENTS -- POR I3010PE : KRd5M 2 r0R PATHWAY: P.UME I ADULT: T. BODY GI-T .t A C T BONi L.l V E R KIDNEY TEYRCID LUNG j CHILO: TEfN! 2.63E+01 2.403+02 2.60E+01 2.604+J1 2.60E+01 j.600+01'{.66E*01 7 66 $+01 KIN' INFANT: 2.e3E*01 2.60!+J1 2 60l+0L 2.401*01 I.60E+01 ..o01+01 +.coE+01 7.66 +01 2 60E+01 2.30!+01 2.60t+01 2 303+01 2.601+01 2.60!+01 2.66E+01 T . 6 6 + 31 2.63E+01 2.40!?01 2.60E+01 2.60s-01 2 60E+01 2.60!+01 2 6eE+01 T.665*01 i POR PATHd,AY: G1CUN0 ADULT: T. 5007 GI-TRACT 30N! LIV!R KIONEY THYR 0!6
- LUM 3 TEEN: 0.03E+00 0.00!+00 0.00!+0J 0.00!+00 0 00E+00 0.00i+00 0.00E+00 0.00!+003AIN
}"NPANT:
MILD: 0.03E+00 0.03E+00 0. 0.002+00 0 0 !* 3 0 0.03E+00
- 0. 0 0 !+ 0 0 3. 3.00-0 0 :g+00 + 00.00E+00 0 0. 0 0 E +30 00 0!+ 00+ 0.00E
- 0. 0 0! 0 0 0. 00+E00 + 00.00!*30 0
0 03E+00 0.J0!+00 0.00!+00 0.00!+00 0 00E+03 0.00i+00 0.00f+00 00. 00!+00 00e+00 POR PAYHWAY: V!GITA8LE AQULT: T. 60DY GI-TRACT BONE LIVER KIDNEY T1Yt0!O LUNG SKIN TEfN: 0.03E+00 0 0.00!+00 0.00i+0J 03*+00.0.008+00 0.00E+003.00!+00 0 00* 0.00E+03 0.003+00 0.00E+00 0. 0 0!+ 0 0
.CHILO: 0.03E+00'0.00!*00 0.00E+00 0.00!++00 0.90 +0000 0.g3 +00 0.00f+00 0.002+00 0.00*
INFANT: ,
- 0. 00s+ 0 0 0.00E+00 0. J 0 ! ++ 00 0 0 0.03E+00 0.00!+00 0.00f+00 0 00i+ 0 0 0. 00 + 00 0.0 0!+ 0 0 0.00E + 00 0. 0 0f +00 POR PATHWAY: M!AT ADULT: T. BODY GI-TRACT 8 0N! . LIVER KION!T THYROID
' LUNG SKIN TE N: 0.03E+00 0.00i+00 0.00!+00 0.00i+00 0.00!+00 0.00!+00 0.00E+00 0.00!+00 LO: 0.0)E+00 0.03E+00 0.00!+00 0.00E+03 0.00!+00 0.00E+00 0 008+00 0.00E+00 0.001+30 , j :CM IN ANT: 0.
0.02E+00 0.Q0!+00 0 2+ 0 00.00*0. 0 000 E ++0 0.00!+00 0 0. 0 0i+ 0 00!+00 0 0 0. 0 0.00!+00 0E + 0 0 0.00E+00 0.00!+00 0.00!+00 0.00E+00 0.00!+00 l POR PATHWAY: C3W MILK JULT: T. B30Y GI-TRACT 3 LIV!R K* THYRCIO LU 0.03E+00 0.30i+00 0. 0 0 l+0 N i00 3.30f+00 0.00pNEY.+00 0.30!+00 0.00E+NG SKIN i 00 0. 0 01+ 0 0 LAffi: INFANT: 8:831:88 8:88!:88 8:88!:88 8:881:88 8:881:88 8:881:88 8:881 0.03f+00 0 00f+00 0. 0 0 E + 0 0 0. 00 !+ 0 0 0. 0 0E+0 0 0. 00!+ 00 0. 00E + 00 0. 0 0 . POR PATHWAY: G3AT MILK
' ADULT: T. SODY GI-TRACT SON! LIVER KIDNEY TdVROID LUNG 0.03E+00 $ KIN TEEN 0 00E+00 g.00!+00 0.00E+00 0.00i+00 0.00 +00 0. 00!+ 00 0. 00E + 00 0.00i+00 CMILD: 0.0JE+00 s 00!+ 0 0 0.00E+00 0.00i+ 00 0.0 0 + 0 0 0.00i+00 0 00E + 0 0 - 0. 00!+ 00 INFANT: 0.00f +00 0.00E+00 0.00E+00 0.00;+00 0.00i+00 0.00E+ 00 0.00 +00 0.00E+ 00 0.00E +00 0.0.00!+00 0 0!+ 0 0 0.00!+00 0.00E+00 0.00!+00 0.00E+00 FOR PATHWAY: IMHALATIO4 ,
ADULT: T. BODY GI-TtACT SQN! LIVER KIONEY- THYRO'D LU SKIN TEiN8 0.03E+00 0 00!+00 0.00E+00 0.00E+00 0.00E+00 0.00E+b0 0 00f+N3 0.03E+00 00 0.00E+00 CHILO: 0.03E+00 0.00*0.00!+00 0. 0 0E+00 0.0 0!+ 00 0.00E+ 00 0 00i+ 00 0.00E +00 0.00!*00 INFANT: 0 03E+00 0.30!++00 0.00E+00 0.00E+00 0.00E+00 0.00!+00 0 00E+00 0 ^0Ievo 00 0.00E+00 0.00E+00 0 00E+00 0 00E+00 0.00E+00 0.60E+00 4 e p e (
- , - #v .- .._ . - . . . - . , . +, - -
]
, : KR87 INDIVIDUAL DO5! F A; TOR 3 FOR 3 A3EDU3 IFFLUENT S -- FOR.....................................................13070PE t
PCR PATHWAY! P.UME T. 80DY GI-TRACT
., ADULT 2 EONE LIV!R KICNEY. THYROID LUNO
- 1. 31 E + 0 2 $ KIN 1.] j:+02 1.31E+02 1. 31 g + 0 2 1. 315 + 0 j 1. g 1 E + 0 2 1.35E+02 4 50E+02 CA!E5:
INFANT: 1: 5'!!:81i: 1.31E+02 1 313.+02 511!ii:li!: 8i 1:ili:82 i:51!:8: i:sli:81 i: lit:Si t:iBl:8i
- 1. J 1 E + 0 2 1. 311+ 0 2 1.315 + 0 2 1 31 E+ 0 2 1. 3 5 E + 02 4 60 E + 02 P0k PATHyAY: G40UND ACULT!
T. B00Y GI-TRA*T BONI LIVER KIONEY THYROI7 L UR3 3 KIN TE!N! 0.0)E*00 0. 3 0 !+ 0 0' O. 0 0 E + 0 0 0. 0 0!+ 0 0 0. 0 0f + 0 0 0.00!+00 0.00E+00 0.00!+00 CHILO! 0.03E+00 0.00i+00 0.00E+00 0.00E+00 0.00!+00 0.00!+00 0.00E+00 0.008 00 INFAWT 0. 03 E + 00 0.0 0 !+ 00 0. 0 0E +00 0. 0 0!+ 00 0. 0 0i+ 00. 0. 0 0 3+ 0 0 0. 00 E + 00 0.+0 0.1+ 0 0 0.0)E+00 0.002+00 0.00E+0J 0.00E+00 0.00E+00 0.002+00 0.00E+00 0.00!+00 FOR PATHWAY: V! GETABLE A00LT3 T. SODY GI-TRACT BON! LIV!R KIONEY THYRDID LUN3 $ KIN TE*Nt 0.03E+00 0 00!+00 0. 0 0 E + 0 0 0. 0 0i+ 0 0 0. 0 0!+ 0 0 0. 0 0!+ 0 0 0. 0 0 E + 00 0.00!+00 CHIL32 0.03E+00 0 03E+00 0.30!+00 0:00E+00 0.00*+00 1 0.00l+00 0.00!+00 0.00E+00 0.00i+00 INFANT: 0 03s+00 0.00f*00 0.00E+00 0.00.+00 0.00E+00 0.002+00 0.00E+00 0.000+00 0.30!+00 0 00E +0 0 0. 00!+ 00 0.0 Ji+00 0.00 f*00 0.00E+ 00 0. 00!+ 00 POR PATHWAY: H!AT T. BODY GI-T 4 ACT SONE LIV!R KIONEf THYRDID ADULT 3 0. 0 E + 0 3 0.00t+ LUNG SKIN TE!N! 0. 0 5' E + 00.:0.0 00 0.000+00 1 00 0.00a+00J.0 0 f + 0 0 0.0 0 E+ 0 0 0. 0 0i+ 0 0 0. 00E+ 00 0. 0 0!+ 00 CHILO! 0.036+00 0.00!+00 0.0 0d +00 0 0 0!+ 00 0.00e *000. 00.0 0!* 0i+ 00 0.0 INFANT! 00 v.00E +0 0 0 0 0. 00 00 E+ 0 0 0 ct+ 0 0 0. 0 0a+0 0 g. 0.0JE*00 0.00!+00 0. 0 0 E *0 0 0. 0 0 f
- 0 0 0.0 0!+ 0 0 0.00f + 00 0. 00 E+ 00 0.0 0f + 0 0 FOR PATHWAY: C3W MILK T. E 00Y GI-T4A;T BON! LIV 3R~
3 ULT! KIONEY THYRCIO . LUN3 3 KIN
.EEN: 0.03E+00 0. 3 0 !+ 0 0 0. 0 0E + 0 0 0. 0 0!+ 0 0 0.0 0E*0 0 0. 00!+ 00 0.00E + 00 0.00E+00 i
CHILO! 0.03E+00 0.03E+00 0.00 f+00 0.00E *00 0.00E+ 00 0.00E+0u 0 00g+00 0.00E +00 0.00!+00 0.00f+00 INFANT 3 0. 00 E+ 00 0. 00E+ 0 0 0. 00E+ 0 0 0. 0 0.+ 00 0. 00 E +00 0. 0 0!+ 0 0
- 0. 00 E + 0 0 0. 0 0!* 3 0 0. 0 0 E+ 0 0 J. 0 0 E+ 0 0 0. 0 0!+ 00 0. 0 0!+ 0 0 0. 00E + 00 0. 0 0i+ C 0 FOR PATHWAY: G3AT MILK
' ADULTi T. 6 0DY GI-TRACT SON! LIVER KION!Y THYR 010 LUNG SKIN TE C H.gLO:
N: 0.03h+00 0.00E+00 0. 0 0 E + 0 0 0. 0 06 + 0 0 0. 0 0E+00 0.0 0!+ 0 0 0. 00E +00 0.00!+00
- 0. 03 E+ 0 0 0. 00 { + 0 0 0.00E+00 0.00E+00 0.00!+00 0.00!+00-0.00E+00 0.00!+00 INFANT! 0.0]E+00 0.30:+00 0.00E+00 0.000+00.0.00E+00 0.008+00 0.00E+00 0.00!+00 0.03E+00 0.00!+00 0.004^00 0 005+00 0 00!+00 0.00E+00 0.00E +00 0.00!+00 FOR PATHWAY: IMH ALATION AOULT:
T. 6 0DY GI-TRACT BONI LIV!R KIONEY THYROID LUN3 -
'5 KIN TEEN: 0.03E+00 0.00!+00 0.00E+00 0.00i+00 0.00!+00 0.00!+00 0.00E+00 0.00i+00 CHILDt 0 03E +00 0.00 f +00 0.00E+00 0.00E+ 00 0.00E+00 0.00!+00 0.00E+00 0.00E+00 INFANT: 0.00E 00 0 00 i+ 00 0.0 0E +00 0.00!+ 00 0.00E+00 0 00E+ 0 0 0.00E +00 0 0 0!+ 00 0 03E+00 0.00i+00 0.00E+00 0.00E+00 0.00E*00 0.00E+00 0.00E+00 0.00E+00 i
l l 9 4 1
4 a
'NDIVIOUAL 005! FACTOR 5 F04 4A$EOU$ 2FFLUENTS -- FOR 130 TOPE : KRad FOR PATHWAY: P.U M E T. cdOY GI-TRACT BON! LIV 2R KIONEY THYRDID LUNG $ KIN
- 5. ADULT: 3. 2!,E + 0 2 3. { e 2 + 0 2 3 2 6 5 + 0 2- 3. 2 6 d+ 0 2 3 26E+0 3.i>* 02 3. 65+02 3 26E*02 3.265+02 3.2tE*0;
, TE!N:
CHILO: c33.264+02 262+02 3.27E+02 3.27E+024.50E+02 4.301+0i l INFANT: 3.25]++02 3 263+02 3.26!+02 3 262+ 02 3.26E+02 3 262+02 3.27E+02 4 50! ' 3 1.22+02 3.263+02 3 26E+02 3.265+02 3.26E+02 3.266+02 3.275+02 4.30E+02 ' FOR PATMkeY: C10UND T. 6 00Y GI-TRACT 50!;E LIVER K!DNEY TMYRO 3' D' 0 00i+$ KIN ADULT: L U N'G YEEN: 0.00E+00 0.0 0 2* 0 0 0.00 E+ 00 0.0 Ci+ 00 0.0 0E+ 00 0. 0 0 E0+0.00!+00 00 i CHILD: 0. 0 3 E + 0 0 0. 0 0 54 0 0 0. 0 0 E + 0 0 0. 0 0 f + 0 0 0.00E+00 0.00!+00 0.00E+00 0 00i+00 } INFANT! 0.03E+00 0.00!+00 0.00E+00 0.00!+00 0 00E+00 0.00i+00 0 00E+00 0.00* 00 0.03E+00 0.002+00 0.00E+00 0.005+00 0.00E+00 0.00!+00 0.00E+00 0.00l++00 FOR PATHWAY: V!G! TABLE ADULT! T. BCDY GI-TRACT BON! LIV!R KIONEY THYAOIC LUNG SKIN i TEEN: 0.03E+00 0.003+00 0. 0 0 E + 00 0. 0 0!+ 0 0 0. 0 0 E+ 0 0 0. 0 0!+ 0 0 0. 00 E + 00 0. 0 0i+ 0 0 i CHILD: 0.00E+00 0.00!+00 0.00!+00 0.00!+00 0.00E+00 0.J0E+00 0.00E+00 0.00E+00 ' INFANT: , 0.00E + 00 0.00i+00 0. 0 0E +0 0 0. 00!+ JO 0.00!+00 0.00f+00 0.00E+00 0.00f+00 l 0.03E+00 0. 0 0 3+ 0 0 0. 0 0E + 0 0 0.0 0!+ 0 0 0. 0 0E+ 00 0.0 0E+ 0 0 0.00E + 00 0 00!+00 ' FOR PATHWAY: M!AT T. SODY GI-TRA*T SONE LIVER KIONEY THYROIO LUNG SKIN AQULT: 0.00* Tc N: 0.03E++00 00 0 0.00i+00 0.00E+00 0 0 !+ JO0.00E+00
- 0. 0 0E+00.00* 00.00!+00
- 0. 00i+ 00.006+00 0 0.00E+00 0.00!+00 0.0Ci+00 0.00E+00 0. 0 0 6+ 0 0 0.00t+00 0.00i+00 CM LD: !
IN ANT: 0. 0 3 *E 0.03 00++0 00 00 0. !+ 00 00 E 0.+0 00 0E + 00 0. 0 0i++ 0 0 0. 0 0 E0.005+00 00 0.00E+00 + 0 0 0.00i+00 0.00E+00 0.00E+00 . 00i+00 0.00!+00 FOR PATHWAY: COW MILK T. S ODY GI-TRACT SONE LIVER K I C'4 E Y TdVRDIO LUNG SKIN j JULT*
# E ! *. 8 0. 0 3 E + 0 0 0. 0 0 d 0.03E+00 0.00!*00 0.00 00 0.00* + 0 0 0. 0 0 f + 00 0. 0 0i + 0 0 0. 0 0!+ 0 0 0.00i+00 4.00E+00 0.00:+00 i CPALO: 0. 0 0 E + 0 0 0. 0 0 E + 0 0 0.
+ 0 0 t + 0 0 00 0. 00 0!++ 0 0 0.0.005+00 0 0 E + 0 0.00$+00 0 0.00!+300.00E+00 4.00E+00 0.00 !
IWPANT: 00E+00
- 0. 01E + 00 0 0 0 !+ 0 0 0. 0 0 E + 0 0 0.00E+00 0.00E+00 0. 0 03+ 00 0. 00E + 00 0.00i+00 '
l FOR PATHWAY: G3AT MILK I
? T. BODY GI-TRACT BONE LIVER KIONEY THYROID LUN3 3 KIN 1
ADULT: 0.03E+00 0300f+00 0.00!+00 0.00* i TEEN: 0.00i+00 CHILD: 0. 0 3 E + 0 0 0. 0 0 i+ 0 0 0 0 0 E + 0 0 0. 00 E++ 0 0 0. 0 0 *+ 0 0 0. 0 0 3 + 0 INFANT: 0.00E
- 0. 00 E+00 + 0 00 0.
0003+00 0i+ 0 0.00 0. 0!+00 0 0E +00 00i+ 0 0.0 00 0!+0.00E+00 0 0 0.00E +00 0. 000.E+ 0 0i+0000
- 0. 0, 0000EE ++00 000.00i+00 0.00i+00 FOR PATHWAY: 11HALATION T. BODY GI-TRACT BON! LIVER KIONEY TnVROID LUNG SKIN ADULT:
TEEN: 0.00E+00 0.003+00 0.00E+00 0.0 0!+ 0 0 0.0 0E + 00 0.0 0 f + 00 0.00E + 00 0.00E+00 CHILD: 0.03E+00 0.00!+00 0. 0 0E +0 0 0.00E+ 0 0 .0.0 0E + 00 0 00i+00 0.00E+00 0.005+00 INFANT: 0.03E+00 0.00i+00 0.00E+00 0.00E+00 0.00E+00 0.00!+00 0.00E+00 0.00E+00 i 0.00E+00 0.00i+00 0.00!+00 0.00!+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 l \; . l i 1 l i
. l l . j
.;i
+
J INDIVIOUAL D0$! FACTORS FOR GA3EQU$ SF8LUENT3 -- FOR 130 TOPE : KR39
.OR PATHWAY: P.UME T. BODY GI-TRACT BON! LIVER KIONEY T H'Y t 010 LuN3 SKIN 1 ADULT: 3. 6 3 E + 0 2 3.685+02 3.64E+02 3.68E+02 TEfN! 3.6dE+02 3.625+02 3.66E+02 3.685+02 .6SE+0 .6dE+02 3.68E+02 3.72E+02 7 . 4 6 E + 0 2
- - .-, -- -,.-----.-e, --
h l . i , 004900'0 00+300'0 00+700*0 00+U00 *0 00+700'C 00+300 *0 0C+E00'0 00+3C0'0 :1NVdNI l00*300'0 00+300*0 00+700*0 00+0C0*0 00+700'0 00+i00'0 00+iOC*0 00+300'0 :C11H3 '00*!00'0 00+300*0 00+t0C*0 00+U00*0 00+700'0 00+300'0 00+500'0 00+7CC*0 :N331 004300'0 00+300'0 ' NIMS ON01 00+700'0 00+000*0 00+300'0 00+300*0 00+700*o 00+200'0 :1100V GIQB1H1 ABNFTT MIAll PNCE 13Vti-IS 10r.9 *1 NOIlt1rHkI :AYMHIVd 80d 100+I00
- 00+i00 0000+ 00+300'0 00*0 00+100'0 00+300'0 00+300*0 00+700'0 00+10C*0 00+300'0 00+i00*0 00+700*000+10C*0 00+E0C'000o300'0 00*!C0'0
- 1NVdNT
- 01IH3 009700 00 00+
- 00*300 0 0 00 *0 00 +100
- C 00 +30 0'0 .00 + 00
- C 00+ 300'0 0 0 +F OC'0 0043C0'0
+ 00
- 0 0 0 +5 00
- 0 00 +30 0 '0
= 00 + {C O
- C 0 0+ 30 0
- 0 0 00+1Co*0 0 +10 C *0 :N331
- 1100V .
- NIMS TNn1 OIOVAF1 AINGIM M3All IN09 13 vel-IC A006 *1 .
11IW 4VC0 IAYMH1Vd 30d '00+300'0 00+300*O 00+200'0 C0+300'0 00+300*C 00+300'0 0C+700'0 00+VCo*O :1NVdNI l88:!88*8 700+100'0 88+188:8 88:!88:8 88:188:8 88:!88:8 88:!88:8 88:i88:8 88*!E8:8
'fa!V3 00 + 100
- 0 CIOhAHL 0 0 +F O C *AIK C C 0 +6Il200'0 OC+10C*C :1100
' NIMS ONn1 MEAIl INCECC+300'0 00+20C'0 00+;CO'*0 137ti-IC AOCS ** 1 ( 11IH MC3 :AVmHAVd WCd
- 004700'0 00 + 200 '0 0 C +i0 0 '0 0 0 +10 0 '0 0 0 +30 C
- 0 0 0 +10 0 '0 0 0 +i O C *C C0+300*0 :1NVdNI 00+iCC'0 00+I00'0 00*i00*0 0C*i00'0 00+*Co*C 00+200'0 C1IH3 00*!00'0 0
00+ 300 *0 00 +3 00 *0 0 0 +20 0'0 00 +'00 3
- C - C 0+ 30 0 '0 Oc+3 C C +
0si OO { '* 00+iC0'0 0 00+3Co*0 :N231 N .g *15i00'0 00+300'0 0g+UAH1300*0 0.Q C0+3^110*CWiAI1 00+:0C*C C0+iO0*C 00+icC*C 00+iC0'0 :1100V ONn1 13N0 13Yti-IC ACCE *1 INCE ; IViW :AVM'11Vd WOd '00+700 0 00+ 00* C0'0 21NVdNI !00*]OC 00+ 00* 00+50C*0 00+300'0 00+20C*C 00+100'0 00+joC*C 00+}C0'0 l00+s00 00+ 00* 0 0 + ): 0 g
- 0 00 +20 0'0 0C +!00 '0 C 0+ 30 0 *0 0 0 +s 0 0 *0 00+3 :C12H3
!00*300 00+ 0w'O C0+300'0 00+300*C 00+*:00'0 Oc+iOC'0 00+3CO*0 :Nf31 00+ 00* 00+700'0 00+300'0 00+iO0*C 00+300'0 OC+70C*0 00*3CC*0 .:11n0V -
- NIMS !Nn1 CICBAF1 A3NCIM 35All INCE 10Vti-ID A009 *1
3191130iA AVMHivd 80d I00+200'0 00+300*0 00+i00*C 00+300'0 00+F00'0 00+100'0 Oc+ICC*C 00+3C0'0 #1NYdNI l00*j00'0 00+300*0 00+700*C C0+100*0 00+500*C C0+P00*0 OC+jo0*0 00>3Co*0 :01IH3 l00+ 00'0 00+ 300 *0 00 +700 *0 00+300'0 00+10C*0 00+300'0 00+r0C'0 00+PCO*0 :N331 l
- NIMS 0 0 +10 0 '0 . 0 0 + 30 0 '0 00 +i0 0 '0 0 0 +iC 0 ' 0 0 0 +I0 0 'C 0 0 + 3 0 0
- 0 00+iOC'0 00+3C0'0 :11007 SNn1 SIC 3AW1 ,A itlC I M WEAIl FNCS LOYEl-IC A00E *1 CNnct0 :AYMHIVd kod *
'to+76P't 00+ 79t
- T CC +Ef C * ? 00+3CO *Z 00+1tC *2 00+1f 0 *7 0C + f CC *2 00 + 7f 0 *?
i I
- 1NY .NI !
'IO*i6t*t !!0*i40*t 00+9tt*7 CC*i"C*T *k CC*ifC'Z 00+?f0*7 00+1t0*? 00+F(0*2 00+3f0*? : C 1 *. 4 3 ' TNE31 s 00+3PC*200*
- 10
- e 6 9 *1 00+34t*t OC+3(C*t 00+3CO*7 00+it0*
0*C C0+1C0*Z 00+1t0*7 00+3CO*t Co*iC0'Z 00+:*EC"7 CC+ tC*Z C0+780*2 C0*3f0*2 :1100V iNI15 DNn1 OIOVAk1 ABN011 43A!1 INCS 13Vrt-ID A009 *1 ' 3 W A *. d AVMHIVd 80' . WTCliX : 3d0105! 304 -- $1N301445 SnCESVC E0d SWC1:vd ISCO 1VACIAICNI e P
4 .
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+ .
INDIVIOUAL 0051 FACTOR $ 802 GA520U$ !FFLU:N T 3 -- F O R !$0faPE : XEI33M i FOR PATHWAY: P.UME
$ T. 500Y GI-T4A*T 50N! LIVER KION!Y THYRD 0 LUN3 ADULT: .574+00 5.573+3 3. 71+00 s.57E+00 . 7:+00 $ KIN .]
YifN: .574+00 5 57 +0 5. 7f+00 5.37 +00 . 7 +00 s.57 + 0 6 03E+00 3.36 +0t '3 LD: 5.57E+00 .37 +00 5.!?t+00 3.57 +00 5.57 +00 0 6.03 +00 .96 1 + CMjANT: IN 0 6.03 +00 . 6 1
- 5. 5 ? E
- 0 0 .57)+00 5.571+00 5. 57 E+ 00 5.5 7E+00 .371+00 6.03E+00 3. 6E+ 1 FOR P A T H,W A Y : Gt0UND ,
T. BCDY GI-TRACT SONE LIVER KIDNEY THYR 0fD LVNG 3 KIN
? ADULT: 0. 0 3 E + 0 0 0.30!+00 0. 0 0 e + 0 0 0. 0 0!+ 0 0 0. 0 0!+ 0 0 0.00!+ 0 0.00E+00 0.00 +00
; TE N: ,
0.03E+00 0.00!*000.0000{+00 0 0.00E+00 0.00 +00 0 c + 0 00.00d+
- 0. 0 0l+ 00 0 0 0.0 E+00
+ 0 J C.
CH LO: 0.00E + 00 0.00i+ 0.0 E 0. 0 0.00E+00 0.00!+00
; INFANT: 0.03E +00 0 00!+ 00 0.0 0E+00 0 00!+ 00 0.00E+00 0.00!+ 00 0.00E +00 0 00f+00
., FOR PATHWAY: V!G! TABLE I T. 800Y GI-TRACT SON! LIVER K'ON!Y THYR 0!D LUNG $K A ULT: 0. 0 3 E + 0 0 0.0 +00 0.00E+00 0. 0 0 f + 0 0 0. 0 3 E + 0 0 0.00i+00 0.00E+00 0.00!+6'N 0
'e EN: 0. 0 3E + 0 0 00 0 0.00 +00 0 0 0 + 00 0.0 0t+ 00 0. 00f + J 0 0.0 +00 0.00i+00 l MIL 3: 0.03E+00 0.00 0 0.00 +00 0.00 +00 0.00!+00 0.00E+00 0.0 +00 0.00!*00 INFANT , 0. 0 3 E + 0 0 0.J0!+00 0.00E+00 0.30E+00 0.00E+00 0.00f+00 0.00E+00 0.00!+00 FOR PATHWAY: M!AT T. 50DY GI-T4ACT SON! LIVER KIONEY THYR 0!D LUNG SKIN ADULT 0. 00E + 00 0.00 +00 0. 00 E+ 00 0. 0 02+ 00 0.0 0!e0 0 0. 00 + 00 0.00 E + 00 0.00!+00 TE N: CM LO: 0.03E+00 0.00 +00 0.00!+00 0.00!*00 .00E+00 0.30 +00 0.00E+00 0.00!+00 , l 0. 0 0 E + 0 0 0.J0!+00 0 00E+00 0.00d+00 .00E+00 0.00f+00 0.00E+00 0.00!+00
, 2NFANT: 0.00E+00 0 00!+00 0. 0 0E +0 0 0. 00!+ 00 0.00E+00 0.00!+00 0.00E+00 0.00E+00 FOR PATHWAY: COW MILK
' T. 60DY GI-TRACT BON! L V!R K TdVR0!D LUN6 $ KIN
.0VLT: 0.03E+00 0.00J+00 0.00E+00 0.00 +00 0.08'D95Y E+00 0.00!+00 0.00E+00 0.00i+00
, TEEN: 0.00 00 CHILD: 0 . 0 e0 [ ++ 0 0 0.00!+00 0.00!+00 0.0.0 00f0!+ 0 00.0.0 00i+
+ 00 0!+00000.0.000E 0 *+ 0 00.00!+00
+ 00 0.00!*J00.00E+00 0.00E+00 0.00f+00 0.00!+00 INFANT: 0.03E+00 0.00f+00 0.00E+00 0.00!+00 0.00E+00 0.00f+00 0.00E+00 0.00i+00
, FOR PATHWAY: GOAT MILK j T. B ODY GI-TRACT SON! LIV!R KIONEY THYROID LUNG SKIN +
ADULT: 0. 0 3E + 0 0 0. 0 0 E+ 0 0 0.0 0E + 00 0. 0 0 E+ 00 0.0 0E + 0 0 0. 005+ 00 .00E+00 0.00!+00 TE!N: 0.0)E+00 0.00!+00 0.00E+00 0 00 E+ 00 0.0 0!+ 00 0 00f*00 .00E+00 0 00E+00 , CH LD: 0.03E+00 0.00i+00 0. 0 0 E+ 00 0. 0 0!+ 0 0 0.0 0E+0 0 0. 00 c+ 00 0.00E+00 0.00i+00
. IN ANT: 0 03E+00 0. 00i+00 0.0 0E+00 0.00!+ 00 0.00E+ 0 0 0.00!+ 00 0. 00E + 00 0.00i+00 FOR PATHJAY: 19HALATION T. BODY GI-TRACT SON! LIV!R KIONEY TdYROID LUNG $ KIN
- l. ADULT: 0.03E+00 0.00!+00 0. 0 0 E + 0 0 0. 0 0!+ 00 0. 0 0*+ 0 0 0. 0 0E+ 0 0 0. 00E + 00 0.00 +00 TEEN: 0.00&+00 0.00!+00 0.0 0E+00 0.00!+ 00 0.00l+ 00 0.00*+00 0.00E+00 0.00 +00 CHILD: 0.03E+00 0. 0 0 i+ 0 0 0. 0 0E + 00 0. 0 0 E + 0 0 0. 0 0t+0 0 0.00I+00 0 00E+00 0.0 i+00 INFANT: 0.03E+00 J.0 0i+ 00 0.0 0E +0 0 0. 0 0!+ 0 0 0.00t+ 0 0 0 00!+00 0.00E+00 0.0 E+00 i
h 1 1
-1 l' .
. 1
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t l o t l 1 y,. 0e*g00+3C0'0 :1NvdNI 0..,88 .g+g00l88:18l:880: 00+300'0Og+188:l88:'!8:880:g000ce+iOO0Og+188:888:18 ! 5 *?a!V! 00100 0 00+30 IMS ON01 *0 Og+4AN1 040 30C' $0+h00*000+500*000+300*000+50C'0088:1!8:8 A0N01M, NIAll 3NCS 13Vul-IO A009 *1 00+3C0'0 :11007 e NOI1V1THhI 1ATMHIVd WOd (0+300'0 00+ 00 +700 *0 00+300*0g0+300'000+200'000+300'000+3C0'0 21NVdNI b 8*i88:888:l00*l88:188:888:188:808:!!8:888:188:888:i88:888:188:8 00900'0 00+100'0 88: 00+300*0 C0+g00*0 00+300*C 00+300'0 00+I00*0 00+1Co*0
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- 11007 L IMS ON07 OIONAHL 13h-IM ViAll INO3 13Vti-ID AGOS *J P 4
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. . DN01 OICtAML A3N3 M MEAll FN05 13fti-10 A009 *1 ,
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VCO*C 00+ 00*C 00+]C0'0C0'0 C1IW3 .h 0*i00'0~00+000'000+IOC*C00+180*0 IMS- CN01 OIOVAhl A3NOIM 0'0 00+ 00*C OC+ior*C 00+300'0 of+lOr*0 C0+i00*0 00+7C0'0
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'NDIVIDUAL ' 005! FA TOR 3 7 GA$EQU3 ! F .* L U E N T S FCR 130f071 : x
.._______.___._______.___04_______..___.___.___._______.__.____.__!13>M _ ..
; FOR PATHWAY: P.U ME
! T. SODY G1-T1ACT BONE liv 3R KIONEY T4Y2010 s, A LT: LUNG $ KIN
,T N: 6. 9 !+ 01 6.92*+01 6.9 E+01 6 92f+01 6. 9 4 E + 01 4.1 t E + 01 6.95 +01 1.05 +02 CHILD: 6 9 E + 01 c .12 :- )1 6.) E+01 6.1 i+01 6 90E*01 o.) i+01 0.15 +01 1.05 +02 r4 INFANT: 6. 9 2 2 + 01 3.325+01 6.32E+01 6.3 2 01 6.94e+01 6.5 i+01 6.95E+01 1.05 +02 6 92E+01 6.3ki+J1 6.92E+01 6.izi+J) 6.923+01 6.721+01 6.95E+01 1.0$f*02
. FOR PATHWAY: G40VNO 4
'A ULT: T. 800Y GI-71ACT SONI LIV!R KI NEY THYROID LUNG $ KIN T IN: 0.03s+00 0 003+00 0.00E+03 0.00?+00 0.00E+00 0.00i+00 C.00E+00 0. 0 0 i+ 0 0
, L3: - 0.03f+00 0.J0 + 0 0.00E+00 0.00!+00 0.00E+00 0.00i+00 0.00E+00 0.30E+00 ANT: 0 0J. 00 0.30 0.03g*+00 +0 +00 0.30 0. 0 0E + 0 0 0. 00.00d+00 0.00E+00 0i+ 0 0 0. 00.00E+00 0 E + 00 0.0.30f+00 0 0!+ 0 0 0.0.00f+00 03 E + 000.00i+00 0.00f+00
, FOR PATHWAY: V!GZTABLE AO LT: T. BODY GI-TRACT SCN! LIVER K:0NEY THYROIO LUN3 $ KIN
- TE N: 0.03E+00 0.00!+00 0.00E+00 3.00E+00 0.00E+00 0.00!+00 0.00E+00 0.00!+00 CHILO: 0.0J +00 0.00i+00 0.00E+00 0.00!+00 0.00!+00 0.005+00 0.00E+00 . 0 0!+ 0 0 0.0 INFANT:, +00 0.00: 00 0.00E+00 J.00E+00 0.00!+0w 0.00!+00 0.00E+00 .00i+00
' 0. 0 E + 00 0. 0 0 !++ 0 0 0.00E+00 3. 0 02+ 0 0 0. 0 0 E + 0 0 0. 0 0!+ 0 0 0. 00E + 0 9
FOR PATHWAY: M!AT
+
ADULT: T. S00Y G:-TRA T BONE LIV 1R K0 NET THYROIO LUNG SKIN . TE!N: 0 03E +00 0.J 0 f + 0 0 0.00E+00 3.00!+00 0.03E+00 0.J0$+00 0.00&+00 0.00i+00 0.00!+0) 0.00E+03 0.00i+00 0.00E +00 0.003+ 00 MILD: 0 30 5+00 0.00E+00 0. 0*+00 0.0)i+00 0.20!+00 0.00E+00 0.00i+00 0.00E+00 0.00.+00 0.00E+00 0. 0.+ 1 00 hPANT: 0.03E+00 0.3 0 !+ 0 0 0. 0 0E +00 0. 0 0!+ 0 0 0. 0 0E+ 0 0 0. 0 0!+ 0 0 0. 00E + 00 0. 00i+ 0 0 704 PATHWAY: C3W MILK T. BODY G:-TRA;T BONE LIVER KICNEY THYROIO
.00LT: LUNG SKIN ;
TEjN: 0.03E+00 0.0)E+00 0.00!+00 0.00f+300.00E+00 0. 0 0i+ 00 0. 002 +00 0.0 0!+0 0 0.00E +03 0.00E+00 CH4LO' O.0JE+00 0.30i+00 0.00E+00 0. 0 0E + 0 0 0. 0 0i+ 0 0 0.0 0E +00 0. 0 0E+ 0 0 0. 00 E + 00 0. J 0!+ 0 0
, INFANT: 0.30i+00 0.00!+00 0.00i+00 0.00E+00 0.30!+00 0.03f+00 0 00!+30 0. 0 0 E + 0 0 0. 0 0i+ 0 0 0. 0 3E +0 J 0. 00i+ 0C 0. 00E + 00 0. 0 0i+ 00 j FOR PATHWAY: G3AT MILK j T. B ODY GI-TRACT SONE LIVER ADULT: K:0NEY THYROIO LUNG $ KIN
,' CHILD: TE!N: 0.03E+00 0.30!+00 0.00E+00 0.00E+00 0.00E+03 0.00!+00 0.00E+00 0. O!+00 0.03E+00 0.0]E+00 0. 0.00i+00 0 00E+00 0.003+00 0.00*+00 0.00f+00 0.00E+00 0. OE+00
- INFANT
- 00 !+ 0 0 0. 0 0E +0 0 0. 0 0 E+ 0 0 - 03 003+ 00 0. 0 0E+ 0 0 0.00 E + 00 0.00i+00 0.03E+00 0.00i+00 0. 0 0 E+ 00 0. 0 0 E+ 0 0 0. 0 0E+0 0 0. 00i+ 00 0. 00f +00 0. 00 E+ 00 i FCR PATHWAY: IMHALATION .
! T. BODY GI-TRACT AOULT: BON! - LIVER KIONEY TMYRDID LUNG SKIN 1EEN: 0.03E+00 0.0 0!+ 0 0 0. 00E +0 0 0.
- 0. 03 E +00 0.J 0 !+00 0.00E+00 0.00t+00 0 0!+ 00 0.0 0E+ 0 0 0.00 f+ 0 0 0.00E + 0 0 0. 0 0 E+ 00 CHILD: 0.00E+00 0 00E+00 0.00!+00 0 00!+00
,' INFANTt 0. 0 3 E
- 0 0 0. 3 0 i+ 0 0 0. 0 0 E + 00 0.00i+00 0 00E+00 0.00L+00 0.00E+00 0.00Z+00 0 03E+00 0.30!+00 0.00E+00 0.00i+00 0 00E+00 0.00E+00 0.00E+00 0.00E+00 ,
l
l e 00 *F0 0'0 00+300 *0 0 0 +300'0 00+300
- 00+700'0 00+300*0 00+700'0 00+3C0'0 :1NTdNT 00+i00* *2 0 + 3 0 0
- 0 0 0 + 3 0 0
- 0 00+300* 00+
00*300'00 80+300*0 00+200*0 :01IW3 00+500'0 C0+W00* 004700'0 00+300*0 00+300*C 00+300* a.0C'0 C0+300'0 C0+300*0 00+300'0 0C+100*0 00+3Co*0 00+200*0 :N331 NIMS ON01 OICEAH1 ARNOI) 00+700'0 00+300'0 00+500'0 00+3Co*0 211007
, MiAll INCQ 13Vki-IO A009 *1 NOI1V1YHAI 2AYMHIVd Mod 00+300 *0 00+300'0 00+300'0 00 +1C0'0 00+30C *C 00+300'0 00+70C *0 00+ 300'0 21NYdNI 00+[00*0 00+300'0 00+iOC*0 00+300'0 00+300*C 00+300'0 00+f00'0 00+3Co*C :07IW3 00 +2 0 0'0 00 + 700
- 0 00 +200'0 00 +300 *0 00 +7 00 '0 00+70 0'0 00+!0 0'0 00+ 3C O
- 0 N!31 00+E00'0 00+300*0 00+i00*0 00+300'0 00+;00*0 00+300'0 00+20C'0 00+300'0 N!MS ONul CIDEAHl.-A3NOIM MEAIl :11007 INCE 1 vel-10 A009 *1 g
( W1IW 1VCD :AVMW17d V0d , ~0 0 + ? 000+300'0 00+200'0 0 '0 0 0 00+iOC*C
+3 00 '0 0C0+100'0 0 +f 00 '0 00+0 0+i0 0 'C 00 +):00 0C'c 00+100*C 0C+i0*0 00
*0 + 300 '0 0 0 +:1NVdNI 00+300*0 5 0 0 '0 00
- 01IW3 ' +
00+700'0 3 00+300'0 00+iOO*0 00+300'0 0C+200*0 C0+200'0 00+30-(*? 00+3CO*O :N!71 ' OC+^0C*CONC1 9%)$ 00+100*0CIOVAW1 0C+iO0*0A3NG1 00+!0C'0 WiAIl C'C+20C'C 00+300'0 00+s0. 0 00+300*0 :11C05 IN09 13YEl-IO AOCS *1 ; W1IW MC3 AYMH1Yd 40d . 00*F00 *0 00 + 700 *0 00 +00C *C C0+200'0 00 +?C0'0 00+300'0 0C+i0C'c 00+300
- 0 21NVdNI
'0+?0C+0 00+200'0 3C0'0 :C1jw3 OC;*FOC'c 00 **:00*00 +r 0 0 '0 0g0 + 300'0 00*30C '0 C0+200*0 00+3C0'0 Oc+F00'c 00+!00'0 C0+100'0 00+300*0 OC+ioC*0:00'0 00+ C0+ 00+iCC'0 :N331 0+3u0*0 00+200'0 ONC1 OI0 HAH 1 00+100'0 AEN0:1 OC+iOC'C 00+300'O OC+iCO*C 00+7C0'0 11007 .
@IMS WiAIl ENOS 13Yki-!0 A001 *1 1. LYiW AVMW1Vd 80d C+200 '000+300'0 0*i00'0 00 + 300'000+ 00+300 *0 00+300'0 00+30C'C 00+700*C 00+TCC*0 00+320'0 :1NVdNI C0+3C0'0 :C11W3 ? '00{0C'000'0 C+3 00+300*Ci00'0 00+j0c'O00+300'0 C0+30C*0 00+f0C'0 00+f00'C 00+300'0 00+i00'0 00+iOC*0 00 00+3C0*0
*70C *0 N331 *
. ISS 00+300'0 C0*300'0 CMol 0101AF1 00+300'0 A?NGIN 00+70C'0 00+3C0'0 00+1CC*C 00+3C0'0 :llnov 85All INCE 10f tl-ID A00 9 *1 i 219Y120iA :AYMH1Yd 80d 0 +{0 C0+3C0'0 :1NYdNI i' C +1000 *C 0+: *000'0 00+
00+j0000+300'0 00+P00'0
- C 00 +500 *0 00 00+300'0
+300'0 00 +IOC00+F00*0*g 00+ 00+300*0 00+200'0 700 '0 00+{0f*C C0+}CC'O :Cliw3 300'0 00+iOC*0 00+300'0 00+700*w 00+300*C 00+30C*0 00+=C0'0 :N.-31 '
J0*200'0 p!MS 00+100*0 CN67 00*30C'C 00+300'0 OIckAH1 A,1N 0
- 7 00+30C*C 00+3C0'0 GC+ECC*0 00+3C0'0 11100v :
alA:1 INCE 1 YEl-ID A00 9
- L
~
CNn0k0 :ATMHIVd 80d h 0* 9C*T 0+ 9C* 10+360*4 tc+f c*t to+1?C** 70+760*v tc+i!0*t T0+E7C*t 10+}20*9 TC+ttC*t T0+320**- 0+3 0*9 T0+ito't TC+370*t f 0 + j 'Z C
- t 10+320*t
- 1NTdNI C* +0*tT T0+360*t 0** 3.0*i?C't to+770*1 10+220*t TC+ C** T0+jio't C1IW3 ..
0*19C't 10+160** T 0 TC+1 + 1 'f C '
- Ni31 IMS CNn1 01CVAH1 10+i?C't TC+1!0*? IO+320*t 10+tfC** 10+s20*9 A3N0!1 NEAI1 111n0v 's INOS 1:Tri-ID A008 *1 '
3WA*d ATMMITd WO4 . SitiX : 3dO10!I UC4 ~~ Tife3nledi 50C2570 N0i $3C1:Td it00 1YACIAICNI , f ..
\f
+
~-
*8 l
IN0!VIOUAL 00$$ FACT
..................... ORS FOR GA5EQU$ '2F8LuSNTS -- POR....................... .......... .......2307080
... : x!137 L* FOR PATHWAY: P.U NE l a 1
1 ADULT: T. B00Y GI-72ACT BON! LIVER KIONEY THYRCID LUNG - liK I N t TEEN: CHILJ: 3.3st+01 3.15E+01 3.158+01 3.155+01 3.15E+01 3.15E+01 3.15E+01 3 15!+01 3 1S 01 a3.a58 3.13s+01 01013.15E+013.15E.01 3 15 +01 3.542 sci 4 3 15E+01 3.15 +01 33.54E+01 4..t!+02
.15 3 ++
INFANT: 3 13 E + 01 3 13 2+ 01 3.13.[+ + 013 15! 01 3.13f+01 J .153.15 5 ++ 0 01 54E+01
?. 3.54E+01 4 24f+02 4.zei+02 FCR PATHWAY: Gt0VNO AOULT: T. BODY GI TRA*T BONE LIY!n KION$1 THYRO *3
- LONG $ KIN TEEN: 0.03E*00 0.30!+00 0.00!+00 0.0c!+00 0.00E*00 0.00E+00 0.00E+00 CHILD:
; INFANT: 0.03E
- 00 0 00 i+ 00 0.0 0i+ 0 0 0 00.00E+00 0!+ 000.03E
- 0. 0 0 d+ 0+00 0.0 0 0. 00 E +0i+ 00 0.00 0.0 0 0!+ 0 00!+
" 0 03E+00 0.00!+00 0.00E+00 0.00!+00 0.00E+00 0.00!+00 0.00E+00 0.00E+00 POR PATHWAY: V!GET18LE '
'i ADULT: T. 5007 GI-TRAIT BONS LIVER KIONEY THYROID TEfN: 0.00$+00 0.00!+00 0.00E+06 0.008 LUNG SKIN 0.0)E*00 0.J0* 00 0.00E+00 0.00!+0C00 0.00E+00 0.00 +00 0.00E+00 0 00i+30
' +
CHILO: + INFANT: 0.03E+00 0.003+00 0.00&+00 0.00!+00 0.004+000.00E+00 0.00 +00 0.00E+00 0.00!+ 0 03E+00 0.00!+00 0.00E+03 0.00!+00 0.00E+00 0.00 +00 0.00E+00 0.00E+00 0 00E+00 0.Jos+00 0.003+00 FOR PA'THWAT: M!AT 3 ADULT: T. BODY GI-TRACT SON! LIViR FIONEf TdYROID t TE5N: 0.03E+00
- LUNG $ KIN' l
, CHILO: 0.03E +00 b 00E+00 00!+00 0.00E+00 0.00E*00 0.00!+00 0.J0!+JO 0.00!+00 0 308 0.00!+00 0.005+0C.0 0t+0 h.00!+00 0.00!+00 0 0. 0 04+ 3 0 0. 0 0E + 0 0.00E+00 3 0. 0 0!+ 0 0 0.
j INFANT:
- 0.03E+00 0.00i+00 0 00E+00 0.00!++00 0 00E+00 0.00d+00 0.00E+0000 0.00i+00 FOR ?ATHWAY: C3W MILK "
ACULT: T. BCDY GI-TRACT BCNi LIV!R KIONET THYROID. 1 TE5N: 0.00E+00 LUNG SKIN i CHILD: 0.03E+00 0.00!+00
- 0. 3 0 !+ 000.00!*00 0.0 0! + 0 0 0. 00 E + 00 0. 0 0E + 0 0 0. 00!* 00 0. 00E + 0 0 0. 00 INFANY: G.03f+00 0.00!+00 0.00E+00 0.00i+00 3.30f+00 0.00E+00 0.005+00 0.00E+00 0.00i+00 -
0.00E+00 0.00t+00 0.00E+00 0.J0!+00 i 0 03E+00 0.J03+00 0.00E+00 0.30Z+00 0 00E+00 0 00!+00 0.00E +00 0.00f +00 FOR PATHWAY: G3AT MILK l T. 8 00Y GI-TRA*T t ADULT: BONR LIVER KIDNEY THYROIO LUNG SKIN TEEN: 0.00i+00 CNtLD: 0.03E+000.30!+000.00i+000.00E+00 0.00E+000.00i+00 0.00i+000.00E+00 0.00E+00 0.00E+00 0.00E+00 0.005+00 INhANT: 0.036+00 0.00i+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00&+00 0.00E+00 0.00E+00 0.00!+00 0.00!+00 0.03f +00 0 002+00 0.00E+00 0.00s+00 03 00E+00 0.00!+ 00 0.00E+00 0.00f + F0k PATHWAY: IiMALATION ' i T. BODY GI-TRACT ADULT: BONE LIVER 'KIONEY TdVRDIO LUNG $ KIN TEEN: 0.03E+00 0.00f+000. 03 E + 00 0. 0 0 E+0 0 0.0 0E + 0 0 0. 00i+ 00 0.0 0E+ 0 0.00i+00 ' CHILD: 0.03 E +00 0.00 0.00E+00 0.00E+00 0 00E+00 0.00f+00 0 00E+00 0.00!+00 *
, INFANT: 0 0 0. 0 0E+ 0 0 0. 0 0!+ 00 0.0 0E+ 00 0. 00E+ 0 0 0. 00E + 0 0 0. 0 0!+
t 0.03E+00 0.00E++00 0.00E+00 0.005+00 0.00E+00 0.00E+00 a 9 ( 4 6
,-+eeMA'*'M'
3,;a- -; g ,;, g ;;
, ?t .
'.INOIVIDUAL 035! PACTOR! FCR GAS
_____________._______._________E3US EFFLUENTS 150T03E : x2138 ! __..___________ -___FOR ..__ ___________... rDR PATMWAY: P.UME I T. BODY GI-TRACT SON! LIV!R KIONEY THYROIO LUNG SKI-M 5 ? S q INFANT: 1 96E+02 1.36f.+02 1.96E+02 1.foJ+02 1 96E+0f 1. Jti+ 02 1.94E+0h +
$.f!!+0-
*y FCR PATHWAY: G10 UND T. B 30Y GI-TRACT SON! L V!R KIONEY TMYR0!D LUNG ADULT: SK TE*N: 0.03E+00 0.003+00 0.00t+00 0.00!*00 0. 0 0 E + $ 0 0. 0 0i+ 0 0 0. 0 0 E + 0 3 0. 0 0!+ $' -
CHILD: 0.03 E + 0 0 0. 3 0 + 0 0 0.0 0E + 0 0 0 00!+ 00 0. 0 JE + 00 0. 00!+ 00 0. 00E + 00 0.0 0i+ 0 - 4 INFANT: 0.03E+00 0.00 +00 0.005+0J 0.30i+00 0.00E+00 0 00J+00 0.00f+00 0.00E+0-0 03E+00 0.30 +00 0.00E+00 0.00!+00 0.00t+00-0.00!+00 0.00E+00 0.00!+0-l FOR PATHWAY: y!GETA8LE T. BODY GI-TRACT BON 3 LIY!R KIDNE THYR 010 LUNo SKI AOULT TE!N: 0.0 E+00 0. 0.00* 0.003+00 0.a^E* 0t 0.0C!+ CHILD:
- 0. 0)E J +0 0 0.30!+00 00!+ 0 0.00E++00 0 3.00!+00 00.00E+0 00E+0 0. 00*+ 30 0 6b I' O.00e.0*gc l
INFANT: 0.03E+00 0.002+000.00E+b03.00E+30 0 3.00!+00 0.00E+00 0.30l+00 0.00 +0J U.00i+0? 0.03E+00 0.J0t+00 0.00E+00 3.00!+00 0.00E+00 0. 0 0!+ 0 0 0. 00 +00 0 00!+0/ FOR PATHWAY: M!AT
- T. 800Y 3I-TRACT ELN! - Ljv!R K!0NEY THYROID LUNG Sk
- ADULT 0.03E+00 0.00!+30 0 03E+J) 0.00.+00 i TEEN: 0.03E+03 0.30f+30 0.00E+'e] 0.0c 0.0J8 C3 0.00i+00 0.00i+00 0.30E+0g CHILO: 0.03E+00 0.00E*03 0.30E'+*00 00 C.0.00,+00 t+ 0.00!+00 0.00l+00 0 00E+0 OE+00 0.00E+00 1 INFANT: 0.03E+00h00!+00 00!+00 0.00Ev000.00!+000.h0E*030.00!+000.00E+000.001+00 0 00^+
0.00!+0*
! FOR PATHWAY: C3W MILK
{ OULT T. BODY GI-TRm!T B3N! LIY!R KION!Y THYRDIO LUNG SKID
. **N: 0.03E+03
- 0. 0 3 E + 0 00.3)!+00
- 0. J )
- 000.00E+00 0.00E+00 0.00!+00 0.00E+03 0.00* 00 0.00E+00
+ 0. 0 0 !* 0 0 0. 0 0 E + 0 0 0. 3 0!+ 0 03. 0 0f 0.00!+0 0./
- dMfLO: 0. 0 3 E + 0 0 + 0 003 INFANT: 0.00i+00 0.00!+00 0.00E+00 0.00*
j FOR PATHWAY: 0.03! G3AT +0MILK 0 0 00 f + 0 0 0. 0 0f +0 J 0. 00!+ 00 0.00E+00 0. 00!+ 00 0.00E + 00 0 N T. BODY GI-TRACT BONE LIVER KIONEY TdVROID LUN3 SKI b ADULT: TEEN: 0. 0J E + 0 0 0.0 0 !+ 0 0 0. 0 0 E+ 0 0 0. 0 0!+ 0 0 0. 0 0E+ 0 0 0. 00 E + 0 0 0. 00 E + 00 0.00!+ CHIL3: 0.0 3 E + 0 0 0.0 0!+ 0 0 0.0 0!+ 00 0.00!+ 00 0.0 0E+ 0 0 0.0 0!+0 0 0.00E + 0 0 0. 00 E+ 0 INFANT: 0. 03E +00 0.001+ 00 0. 0 0E + 00 0. 00!+ 00 0. 0 0 E+00 0. 005+ 00 0.00E + 0C 0.00!+J 0.03E+00 0.00!+00 0.00E+00 0.00i+00 0.00E+00 0.00Z+00 0.00E+00 0.00E+3;,
. FOR PATHWAY: IMHALATION h T. SODY GI-TRACT 80N! LIVER 'IDNEY K TMYROID LUNG SKI AOULT:
TEEN: 0. 03 E + 0 0 0. 0 03+ 0 0 0. 0 0 E+0 0 0. 0 0!+ 00 0.00d+00 0.00E+00 0.00E+00 0.00E+0* CHIL3: 0. 03 E + 00 0.03E+00 0.0 000 0.00 h*+ 0 0 0. 00.00* 0.00l+00 0E + 00 0. 0 0!+ 00 0. 0 0d+00 0 00E+00 0.00E+ INFANT: 0.03E+00 0.00f+00 0.00t+00 0.00!++00 000.001+00 0.001+000.00E+00 0.00f+00 0 00E+00 0.002+0 0.00E+00 0.00i+0a/ i l
. I
~
L 6 _, , , . ~ rr- ~
.?'
2 0
!NOIVIDUAL DC5! FAIT 0A3 FOR SA3EDU$ !FPLUENTS -- FDR 1507075 CR$1
~
, FOR PATHJAY: P.URE I T. 60DY GI-72ACT s' ADULTt BON! LIV!R KIONEY THYROID LUNG SKIN
' TE!N 0.03E + 00 0.002+00 0.00E+00 0.00!+00 0.00E*00 0.002+00 0.00E+00 0.00!+00
. , ' jMILD 0.03!+00 0 30 E+ 0 0 0. 0 0!+ 0 0 0. 0 0!+ 0 0 0. 0 0E + 0 0 0.003 00 0.00E+00 0.00!+00 g NPANT! 0.03E+00 0.00i+00 0.00E+00 0.00!+00 0.00E+00 0.00!+00 0.00E+00 0.00f+00 '
0.03E+00 0.003+00 0 00E+00 0.00f+00 0.00!+00 0.00f+00 0 00E+00 0.00i+00 g FCR PATKWAY3 GtCUN3 T. BODY GI-TRACT 1.43E+05 1. 4 3 3 + 0 5 1. 4 3 E + 0 5 1.LIV!R ADULT! TON! . KIDNEY THYROI'0 LVNG SKIN TE8N: 1.43E+05 ~ 1.63* 4 3 f + 0 5 1. 4 3 E + 0 5 1. 4 3 :* 0 5 1. 43d+05 1.69E+05
. CHILD: 1.43E+05 1. 3!++05 1.43E+05 1.*35+05 1.4tE+05 1.43I+3 1.431+05 1 692+00 t INFANT! 35 1 43E+03 1.43E+05 1.43E+05 1.43f+0 1.431+05 1.691+0*
1.43E+05 1.42t+05 1.43!+05 1.43E+05 1.63t+05 1.432+0 1.43E+05 1.oSE+0! FOR PATHWAY: V!GETAELE A ADULTp T. 60DY GI-TRA0T SONE LIVER K THYRD'O LUN3 SKIN 1.05 E+02 s t TE8N1 CMlLD2 1. 5 $ :{ ++ 0 3 2. o 13 +0000E+00 0.00E+00 503 2.663+053.40!+0' 3.el!*J2 0.00!+00 2 21H+03 0.00E+00 0.00!+002 3 INFANT!, 3.05E+03 1.6:1+05 0.00!+00 9.00E+00 4 631+03 1 70!+03 3 10d+03 0. 0 0!+ J O 4 0.00f+00 0.00!*00 0 00E*00 0.00!+00 0.00E+00 0.00f+00 0 00E+00 0.00!+00
'.j' FCR PATHWAYS f
M!AT
% T. BODY GI-TRACT ADULT: BONE LIV!R KICNEY THYROID LUNG SKIN l TEEN 2 1.29E+02 1.03E+02 3.I3f+04 1.7!!+040.00E+00 0.00 +00 0.002+00 0.00!+00 2.83E+01 7 63*+01 1.71E+02 0 00E+00
, CHILO:
1 60E+02 3.30!+03 0.00 +00 0.00i+00 .43l+01 8.708 .23E+01 5.715+01 1 478 02 0.00f+00 0.00E +00 0.00!+00 0.00 +00 0 000+00 .00t+00 01 ' (1 INFANT 3 0.00!++00 0.00E+001 0.00!+00 6 lFOR PATHWAY C3W MILK 40VLT: T. BODY GI-TRACT &ON! LIVER KIDNEY TMYRCID LUNG SKIN
'VE!N! 5.2)E+02 9 09E+02 11 31!+05 0.00E+00 0.00E*00 1.13E+02 335+05 0.00F+00 0.006,00 1.99E+02 5.05e+02 1 30E+03 0.00!+003 11d+02 6.91E+02 0 00f+00 i CHILD 2 1.83f+03 9 33!+06 0.00E+00 0.00!+00 2.81E+02 1.03!+03 1.88E+03 INFANT! 0. 0 0i+ 0 0 2.94E+05 6.56!+04 0. 0 0'e + 00 0. 0 0 i+ 0 0 4 19 E + 0 2 1.12 t + 0 3 3.T3 E + 03 0.00!+00 i
FOR PATHWAY: G3AT MILK
.) . 'y ADULT:
T. BODY GI-TRACT SON! LIY!R KIDNEY TdYRDID LUNG SKIN TE!N 6.24E+01 1.5T3+04 0.00E+00 1.09E+02 1. S 3 2+ 0 4 0.00E+00 0.00E+ 00 1 3 9E+ CHILD: 0.00E+00 2.351+01 3.73!+01 8.29E+01 01 e.068+01 1.56E+02 0.00!+00 0.00E+00 , INFANT: 2.22E+02 1 148+04 C.00E+00 0.00E+00 3.37E+01 1.23E+02 2.25l+02 0.00*+00 3 52E+02 1.02!+04 0.00f+00.0.J0E+00 $.02t+01 2.30!+02 4.47t+02 0.00!+00 l FOR PATHWAY: IMHALATICN AOULT: T. BODY GI-TRACT SONE LIVER KIDNEY TdYRDID LUNG SKIN TE!N: 3.17 E
- 0 0 1. 0 51+ 0 2 0. 0 0 J + 0 0 0. 0 0! + 0 0 T. 2 3 E-01 1. 9 9 t + 0 0 4. 5 61+ 0 2 0. 0 0 '+ 0 0 CHILD: 4.292+00
- 4. 8)E +0 0 9.512+01
- 3. 44 0.00d+00 0.00f+00 9.T4E-01 INFANT: 2. 8 4 E + 0 0 1.13 $'++0.000+00 0101 0.00H+00 0.00E+00 I'1 42g+00 T.711-01 34E+00 5 6.64H+0' 71 +00 4.070+02 38 0.G0!+00 0.00E+001+03 0.00!+00 4.19t-01 .
9 .E . 3 4 6
. - - . ,, .,, - .-,n.,--~n,-. , - - - -
. ,d*5' l .
, '. t IN0!v! DUAL 00$! P A; TOR $ r.02 G ASEQUS EFFLUENTS -- POR !$0 TOPE 1 HN54 POR PATHWAYS P'. UNE d
I AOULTt T. BODY GI-TRACT SON! LIVER K!DNEY 'T HY t 01D LUN3 SKIT 1 I - liitit INFANT! 0.03E+00 0.00!+00 0.00E+00 0 00E+00 0.03E+00 0.00 +00 0.00E+00 0.00*+0' 8: 31:88 8:881:38 8:881:88 8:881:38 8:881:88 8:88 881*888:881:8: :88 POR PATHWAYS G10VND
- 0. 3E + 00 0 0 0 !* 0 0 0. C O E + 0 0 0 0 0!+ 0 0 0. 0 0E+ L
*- , ADULT! T. BODY GI-TRACT BON! LIVER KIDN!Y THY 40TD 4 23E +07 4.23 E+07 4.2 E +07 4.33E+07 4.2gh+07 4. 23 E+ 07 4 LWNG SKI TEEN! 31+07 4.94E+0 b CHIL31 4 2 E + 0 7. 4. 2 3 E + 07 4.2 E+07 4.23f+07 4. . !+07 4 33E+07 4 3E+07 4.96 +
4.2 E+07 4.23E+07 4.2 (+07 4 23E+07 4..{3c+07 4.% 32+07 4 3n+07 4.96 +
-l INP ANT! 4 2 E+07 4 233+07 4 23E+07 4 23f+07 4 23d+07 4.23f +07 4.23E+07 4. 96 +
, FOR PATHWAYS V!G1 TABLE
'h{ ADULT 4 1.61E+06 T. B ODY GI+ TRACT BONE LIVER KIONEY THYRDID LUNG SKI E*N: 2.55'+06 1' 54*+J7 I 0.0 0 E + 00 3.4 3 8+ 06 2.51E+ 06 0 0 0 *+ 0 0 0.00h +00 0. +0-HILot 61.+07 0.00E+00 1. 7.3+07 3. DOE +06 0.00.+001
) NPANT! $.05E+06 1.591+07 0.00t+00 1. 9E+07 5.a0f+0e 0.00 + 0 000+00 0.00 00 +0-
+0-i
- 0 03E+00 0.003+00 0.00d+00 0. Of + 00 0.90E+00 0. 00[*00 0.00l+00 0.00
. 00 0.00'E+00 0.00f+0a POR PATHWAY 3 M!AT T5 T. BODY GI-TRACT
'". ADULT 3. 21 E + 04 SONE LIV!R KIONEY TdYROID LUNG SKI
.161+05 0 00E+00 1.68E+05 5.0
' lAitit 1:l!!:81{1:115!!8:881:88 11'81!:f}E+04 0.00!+000.03E+000.00E+0i yf INFANT! 0.03E+00 0.00!:00 + 0 00E+00 + h: l:828:88!:888:801:8'8:88i:8'
.00k:00000E+000.00!+000.00f+0800 1 POR PATHWAY 3 C3W MILK
.I T. EODY GI-T4ACT ADULT! $3NJ LIVER K!DNEY THYROID LUNG TE!NI SK14 CHIL31 2.
5.1)E+04 9 4 E +5.275+05 04 4.753+05 0. 00E.375 0.00E+00 + 00 1. 34 !+ 05 40.00* 5 9 E+ 04 0.00!+00 0.00E+00 0.00 1 0t!+05 3.234+05 0.00E+00 . 3 5 3 ++7.67t+04 INFANT! 1 6ZE+05 2.633+05 0.00E +00 .153+05 1.59E+05 0.00!++00 0 505 1.0!E+05 0.00E+000.00g*+0 00 0.00E+00 0.00!+0a 0.00f+00 0.00f+00 0.00c+0 /
*}PCRPATHWAYI G3AT MILK '
ki T. BODY GI-T R ACT BONE LIVER fu ADULTt KIDNEY- THYRDID LUNG SKIO TEfNt 3.53E+03 6.33d+04 5.671+04 0.00E+00 0.00E+00 3.094+04 1.45d+04 95 51&+03 0.00E+00 0.00E+00 0.00i+06 CHILDt 6.12E*03 1.23E+04 3. 3 7.3 + 0 4 0l+03 0.00E+00 0.00E+00 0.00i+0 INPANT! 1.95E+04 3 15!+04 00.00!+00 00E*00 8.5st+04 4.60!+04 1. 1 Ot+049E+04 0.00d*00 0.00E+00 0.00E+0 0.00E+00 0.00E+00 0.00!+0 PDR PATHWAY 3 11HALATIO1
.- -ADULT 3 T. SODY GI-TRACT SON! LIVER 'KIONEY THYROID 2.03E+02 .45 3+03 0 00E+00 ,,.268+0 3.12 +02 00 +00 4.44E+04 LUNG $KIU TEEN! 2. .123+0 0 00E+ .00c+00
'CHILDI 3.66t+02 0tt+0 .I64+0 0.00E+00 :,.62f+0 00 :,.36 +0 4 03 +0 3 0.0 .[.+00 6 49E+04 .00E+00l ;
INFANTI' 3.14 +0 1.5dE+0.) 2.24!+0 0 00E+00 0.03.g+02 1.54E+0a 0.004+00 3.17&+04p 0 0 .00f+00' . 0 0 E +
*+00 5.uCE+04 0 01 e.
U
't
,. +
I e
)
M l
~ ~ ~ ~ ~ ~ ~ ~- ~ ~~ ~ ^ ^ ~ ' ~ - - ~ ~ -
f1
- U iIODIVIDUAL 005E FACTOR $ FOR GA5EDUS EF+LUE.tf5 -- FOR 15070PE 'i OR PATHWAY: P.UME T. BODY GI-TRACT 1' ADULT! 60HE L KION!Y THYR 0!D
' TEEN: 0 0 0 E + 0 0 .00* 0. 0 0 00 !+ 0 0 0 0 0 E + 0 0 0. 0 0.{ V E R LUN1 SKIN t CHILD: 0.0JE+00 +00 0.00E+00 0.00i+00 0 00E*00 '
INFANT: 0.0)!+00 . 3 0 3 ++ 00.0 0 0 E + 0 0 0 0 C 8 + 00 0. 0 0E+ 0 0 0. 0 0 8+ 0 0 0. 0 0f + 00 0.0 0 03E+00 .00!+00 0.00E+00 00 0.00E+00 0.00E+00 0.00f+00 0.005 00 f*.., POR PA THWAY: GROUND
~ 0.00!+00 0 0.00!+00 00!+00 0 00t+ 0.00%+00 0.00!+00 0.00E+00 0. 0 0l ++ 0 0 , ;
' I q AQULT: T. B ODY GI-TRACT BON!- LIVER KIDNEY TE8N: THYRDIC LUNG SKIN CHILD: 1.15E+07 1.15E+07 1.164+07 1.168 07 1 162+07 1 16E+07 1 1 16E+07 1.168+07 1.16 E+ 0 7 1.16
; INFANT: 1 15E+07 1.16E+07 1.16E+07 1 16{+07
+
lo:+07 1.16E+07 1.165+07 1 16E+07 1.56 07 1.15 s + 0 7 1 16 5 + 07 1.16 2+0 7 1 16 E+ 0 71 1.168 16i+ 0 7+1.161 0 71+ 16!+07 1 36 0 57+2.16 0 7 !* POR PATHWAY: Y! GETABLE s i AQULT! T. 800Y GI-TRA T BON! LIVER K*0N!Y 1.75E+05 1.595+07 THYRCIO LUNG , TE8N:
.i CHfLO 2.72i+06 1.43 +07 0 00E+00 7.95f+05 0.00E+00 0.00i+00 0.00E+00 0. 0 0 ESKIN +00
'e INFANT: 0 0.00!+00 1.18E+06 00E+00 1.04 +07 0.00E+00 1.775+06 0300E+00 0. 00!+ 00 0.00E+00 5.43E+06 0.00E+00 0.00!+00 0.00E+00 0.00* 00
- 0. 0 0 ! ++ 0 0 FOR PATHWAY: M!AT 0.00 +00 0.00f +00 0.00i+ 00 0.00E+ 00 0.00E+00 0 00E + 000.00i+00 M A00LT: T. 80DY GI-TRACT EONi LIVER KICNEY T E 8N: THYRDID LUND 3 KIN
4.1 CHILD
5.7)f*05 7.30E+05 6 3.648 50!+06 06 0.00E+00 0.00E+00 3.26E+05 0.00E+00 0. 00!+ 00 0. 00 '
; INF ANT: 6 99t+03 1. 71 !++ 0 6 0.00f+00 .{ 5a2+05 0.00f+CD 0.00!+00 0.00E+00 0.00i+00 9
0.00E +00 0 00!+ 00 Oc 0 0E +00 0.0bif1+00 + 050.00f*00 0.00t + 0]0. 00l+ 0.008+00 0.00E+00
, FOR PATHWAY: COW MILK 00 0. 00! + 0 0 0. 0 0 t + 0 0 0 00f+00 '
l
'00LT T. B ODY GI-TRA;T Boht LIV!R KIONEY THYRDIO LONG f!N: SKIN
- odILD:
. INFANT:
1 37E+05 3.27E+03 6.63E+03 1.201.712+06 1.155+06 8 0.00E+00 0.00!+00 1.4j!+05 0.00!+00 8.42!+04 0.00E*00 2.ls 0.00c+008+05 0.00i+00 0.00i+00 0.00E+00 0.00! 0.00!+00 0.00!+
- 1. 0 3 E + 0 6 1. 0 8 06 3 ++ 0 6 0.00i+00 0.00!+00 0. 0 0!+ 0 0
*FOR PATHWAY: GOA T MILK 0.00!+00 4.33E+05 0 00E+00 0.00i+00 0.00!+00 0.00!+00 ' Ti w AQULT: T. 500Y GI-TtACT BCNE LIVER TEfN: 2.25E+04 2.05!+05 0.002+00 1.015+04 0 0KIONEY 0 g ++ 0 0 THYRDIO LUNG
- 0. 0 0 E+ 0 0 0. 0 0 E + 0 0 0.00!+00 SKIN CHILO: 3.92E+04 2.35E+35 0.00E+00 1 70E+04
. INFANT: 7.95E+04 1.522+05 0.00E+00 0.00. 00 0.00E+00 0.00E+00 0 00E+00 1 30!+05 1.30i+05 0.00i+00 I' 60i+04 0 00E+00 0.00E+00 0.00E+00 0.00!+00 .
}FORPATHWAY: IVHALATION 20i+04 0.00E+00 0.00E+00 0.00E+00 0. 0 0 E+ 0 0 i
AQULT: T. B ODY GI-TtACT BONE LIVER RIONEY
]. TEEN 4 THYROIO LUNG SKIN CHILD:
INFANT: 6.575+01 3.375+03 1.00!+02 8.30E+01 3.02i+03 0.00E+006.573+01 0.00E+00 5.02E+010.00E*00 0.00E+00 0.00!+0042.941 On00!+00 261+ 1.095+03 0 00!+00 5.6 E+01 l 5.77E+01 3.535+02 0.00E*00 3.87'i+01 0.00E+00 0.00!+00 3 51N+04 0.00!+00 0.00E+00 0 00i+00 2.4eE+04 0. 0 0E+ 0 0 6-i I. 0 0 0 o .
.~........n..............,..... ..
-- ., _.m - - - - a ,- ---
yu. .
- INDIVIDUAL 0355 FAITOR3 POR G A5!hus !F8LUENTS -- FOR ISOTOPE 1 C060 t
.CR PATHWAY 2 P.U ME 8
T. 1 BON! LIVER K! NEY ADULT: 0. 0 0 8 00 +00 Y GI-7tA01 THYtDID LUN3 SKI
' 0.jo!+00 0. 0 0 E + 0 0 0. 0 0g+ 0 0 0. 0 0g+ 0 0 0.00E,00 0.00!+0
.IAlti:
' INFANT! 8:83E
- 0. 0il:038
+0011:888:
0 0,3+ 0 0. 0 0! + 0 0 0. 0 0!+ J 0 0. 0 04 0 g.00!+0088!:888:881:88 8:881:88 8:88e:88 8:881:8 0: 0 004 00 0.00E+00 0.00! 1 FOR PATHWAY: Gt0VNO
. A00LT2 T. 40DY GI-Ttd*T 80HJ LIV!R KICN!Y TE!N: 7.0)E+08 7 398+06 3 T.095+0! 7.095+08 7. 0 95+ 0J 7.TiY R O L3 L uNG SKI 0 9 2,0 8 7. 01E + 0 4 8. 34 !+ 0 CHILD 2 7.096+06 7.J9.+0B 7.09E+03 7.098+08 7.0 9{+0J 7. J9 8+ J 6 7.09E +03 4.34E+0 INFANTI 7.0dE+03 7 094+0S 7.096+08 7.091+0d 7.01t+03 7.095+06 7.09E+0d 8. 34 f + 0 i T.06t+04 7.015+04 T.0iE+06 7.0iE+08 7.03E+03 7.095+08 T.01E+0d 8.34E+04 FOR PATHWAY! V!G2 TABLE T. B O SONE LIV!R K:DNEY TdVR3IO A00 Lit 1.02t+DY LU 07 GI-TRACT 8 4s +07 0.00E+00 6 62E*06 0.00E+00 0 00f+00 0.00E+NG 00 SKIN-Clits:
1:1!i:8i1:11:!i8:881:88I:ll80t 8:88!:83 8:881: 8 8:881 INFANT! 0.00E+00 0.00+000.00E+000.00h :881:38 0 00E+00 0.00!+ 0 0.00E+00 0.00!+00 FOR PAT'HWAYt H8AT
*1 T. SODY GI-TRACT SCN! LIV!R K:DNEY TdTROID
*i A00LT3 3.11 E + 0 6 2 65d+07 0.00* 00 1.418 LUNG SKIN'
! TEdN! 2 CMSLD: 3.83E+06 46E+037 1. 1s 6 *' E0.00E+00
+ 0 7 0. 0 0 E ++ 06 0 0 1. 0 90.002+00 0.00d+00 3 ++ 0 60.00&+00 0.00H+00 0.00!+00 0 00 0.00f+00 INFANT! 0. 0 J E + 0 0 0. 0+00 0 3'+0.00E+00 06 1.208* 0e 0.00.!+00 0.008 00 0.00E+00 0.00!+
0.J0!+00 0 00E+00 0.00l++00 0.00E+00 0.00i+00 00 PDR PATHWAY C3W MILK
\DULT! T. 830Y GI-TtA T BON! LIV!R KIONEY TMYRDID LUN 6.73E+05 5.773+06 0.00E+00 3.075+05 0.00E+00 0.00d+00 0.00E+06" 0.00E+00l $ KIN E!N:
CHILD: 1.1TE+06 6.73J+06 0.005.+00 5.Ili+05 0.00t+00 0.00!+00 0.00E+00 0. 0 0 !+ 0 0; INFANT! 2.33E+06 4.442+06 0.00!+00 5.09E+05 0.00!+00 0.00!+00 0.00E+00 0.00!+00l
~ 3 93E+06 3.93f+06 0.00E+00 1.a5E+06 0.0 0E+00 0 00!+ 0 0 0.00E + 00 0. 0 0 ! + 0 01 FCR PATHWAY: G0AT MILK h T. BODY GI-TRACT SON!
S ADULTt LIVER KIDN!Y THYRDID LUNG SKIN TEdN2 8 13E+04 8.148 1.4L!+05 6.13f+05 0.00E+00 3.695+04 0. 0 0!*00 0.0 0!+ 0 0 0. 00E + 00 0.00!+00 CHILD: 2.86E+05 5.37i++05 05 0.000.00+00+00n.g.7$5E+04 0 00E+00 0.003+00 0.00E+00 0.00!+00 INFANT: 4 63E+05 4.711+05 0.00 +00 1.)QE+04 0.' 94 + 0 0 0. 00 E+ 0 0 0. 00 E + 0 0 0. 00!+ 0 0 3 s t+ 05 0.wCE+00 0. 00E+ 00 0.00E +00 0.00&+ 00 FCR PATHWAY: IMHALATION ADULT! T. BODY GI-TRA0T SDN! LIVER ' KIDNEY THYRDID LUNG
. TE!N: 4.6 7 E + 02 9.035+03 0.00E+00 3 45!+02 0.00E+0J 0 00E+00 .89E+05 0. 0 0e$ +00KIN CHILD: 6 2 9E + 0 2 4. 2'i+ 0
- 0.0 0l+00 6.79 5+ 02 0.0 0E+0 0 0. 00 E + 0 0 .7eE+03 0.00E+00 INFANT: 7.15 E +0 2 3. 01E+ 05 0. 0 0e +0 0 4.16 t+ 02 0.0 0E + 00 0 0 0 E+ 0 .26t+05 0 0.00E+00
- 3. 73 E +0 2 1.011+03 0. 0 0 E+ 00 2.34 e+ 02 0.00E+00 0. 0 0E + 0 0 1.43 E + 05 0.00E+00 k
k 4 O i
.. 1
'pJ ; I i
- INDIVIOU AL 0051 F ACTOR 3 FCR GA32005 0F'LUENTS -- FOR ISCTOPE : IN65
- l
,.OR PATHWAY: P'UNE .
- 7. 8007 GI-TRACT BONE LIVER KIONEY T4YR020 LUNG SKIN
- jADULT: 0.00!+00 0.00 +JO 0.00E*00 0.
TEIN: 0 00(+00 0.00 +00 0 00E+00 0.40*+00 0.00E+00 Jol+ 00 0.00!+00 0.00[+00 0.-00 0.00E+00 0.00E+00 !
'.fCHILD: 0.0Je +00 0.00 +00 0.00E+00 0.00 00 0.00!+00 0.00s+00 0. 0 0 E
- 0 0 0. 0 0.j ++ 0 0 0.00E*00 0.00*+000.00!+008.^50E+00 0.00!+00 . 0.00s+00 y INFANT: ,
0.00E+00 0.00i+0C 0.00E+00 0.00t+00 , j FOR PATHWAY: GtouN0 f, T. 500f GI-TRACT 80Ni LIVER KIONEY TdYRCIS LUNG SKIN' iAOULT: 2.2)E +07 2.295+J7 2.291+07 2 295+07 2 292+07 2.295+07 2.29E+07 2.63E+07 iTEEN: 2.29E+07 2 295+07 2.29t+07 2.'9f+07 2.29E+07 2.z92407 2.29E+07 4 63E+07 CHILD: 2.295+07 2.295+07 2.29E+07.1.395+07 2.29E+07 2.29f+07 2.236+07 2 63E+07 INFANT: 2.29E*07 2.292407 2.29E+07 2.295+07 2.2?f+07 2.293+07 2.29E+07 2.931+07
- FOR PATHWAY: V! GETABLE S T. 600Y GI-TRACT BONE LIVfR KIONEY THYt020 LUNG SKIN
- ADULT:
1.53E+07 $ *0!+07 1.10E+07 3 40f+07 2.3+E+0* 0.00!+00 0.00E+00 0.008+00 I
. TEEN: 2.63E+07 I 355+07 1.536+07 3.J2f+07 3.40*+07 0.00!*00 0.00f+00 0.JCl+00 l
, CHILD:,' I N F A N 6.9AE+07 T: 1.395+07 2.95E+07 7.93f+07 5.00E+07 0.0 0i+ 0 0 0. 00t + 0 0 ' O. 0 0!+ 0 0 i 0.00E+00 0.J0!+00 0.00E+00 0.00!*00 0.00E*00 0.0 0!+ 00 0.00E +00 0 00!+00 1 5 FOR PAT'HWAY: M!AT l
$ T. 500f GI-TRACT 40h! L VER KIONEY THYROID LUNG SKIN I ADULT: 1.03E+07 1.50f*07 5.g0E+06 7. 1.60E+07 0.00!+JO 0.00E+00 0.00!+00 2.39{+07 7E*N: 4.54E*06 7.75f+06 67E+0e 1. 0.00f+00
. CHILD: 1.31E+07 3.70!+06 7.915+0a 2.33 11 +J7 +07 1.17t+07.0.00i+00 1.33E+07 0.00!+000.00E+00 0.00E+00 0.00!+00 qINFANT: 0.00E+00 0.002+00 0.00E+00 0 00 +00 0 00E+00 0.002+00 0.00E*00 0.00!+00 FOR PATHWAY: COW MILK i
T. 600Y GI-TRACT SON! LIV!R KIONEY - THYROIO LUNG SKIN OULT: 4.15E*07 5.79E+07 2.89E+07 9.20!+J7 6.13E+07 0.003+00 0.00f+00 0.00!+Jo 5dN: 7.1)*+07 6.53: 9.43
< .f.HILO: 1.6'E+0d . 07I*07?7 + 6.64E+07
- 8. 71 t +0 7 6. {.34*
3 2 i++ 9 8s8 1 4$ ++07 0.00E+00 0d-0.00!+00
.00E+00 0.00!+00
.00E+00 0.00E+00 INFANT: l
- 1. 8 5 E + 0 8 3 3 9 5 + 0 3 1.17 E + 0 3 4. 015 + 0 6 1.95 +03 0. 0 0f + 0 0 .00E+00 0.00E+00 '
i POR PAYHWAY: GOAT MILK h T. B ODY G!-TR ACT BONE LIVER KIONEY THYRDID LUNG SKIN N ADULT: 4.99E+06 6.955+06 3.47E+0e 1.10E+07 7.38 +06 0.00!+00 0.00!+00 0.00!+00 TEEN: 8 63E+06 7.332+06 5 33340e 1. 3 3 3 + 07 1 13 +07 0. 00!+ 00 0. 00E + 0 0 0.00!+00 CHILD: 1.73E+07 4ed95+0e 1.03E+07 2.786+07 1.75 +07 0.00f+00 0.00E+00 0.00i+00 '
, INFANT: 2.22E+07 4.075+07 1 40E+07 6.311+07 2.33E+07 0.00i+00 0.00E+00 0.00!+00 FOR PATHWAY: I4HALATION i
.! T. 600Y GI-TRACT BON! LIVER VIONEY THYRDIO LUNG SKIN
; ADULT:
TEEN: 1. 63 E + 03 1. 6 9 5+ 0 3 1. 03E +0 3 3.2 7 E+ 03 2.L 9E + 0 3 0. 00 E+ 0 0 '.74 5 + 04 0.00E+00 1
- 1. 9d E +03 1.48 i+ 03 1.2 2 f + 0 3 4.24 E+03 2.94E+03 0 00!+00 1.93e+04 0.00e+00 '
! l CHILD: 2.23E+03 5 173+02 1.35E+03 3 59E+03 2.26E+03 0.00E+00 3. 0.00E+00 ) ( , INPANT: 9.45E+02 1.63E+03 6.12E+02 1.96E+03 1.03E+03 0.00E+00 2.36E+04 05E+04 0.00E+00 {; ' 1. o I.i y .
+
p i I$ II 1 I l1 l 1 d.. , , . .. . .. . . . . , . . . . .. ..
- - - - - - - - - _ _ . - . _ _ - - , - - ,----n-,n- - , , . . - -
. . , . , , . . , . , . , - -,,._-,.m ,,m,.- r, , , . . . ,
, , - ~ - - n
n4 &
- l i
INDIVIDUAL 005! FACTOR 3 FOR G A5EOUS EP.*LUE NT S -- F OR -ISOYOP E t $te)
..OR PATHWAY P.UME T. 500Y 31-TRACT BON! LIV!R KIDMEY TdYACID LUN3 SKIN
.83 ADULT 2 0.00E+00 0.00!+00 0.00E+00 0.00!+00 0.00E*00 0.008+00 0.00E+00 0.00!+00 TE N2 0.00E +00 0.00!+00 0.00E*00 0 00f+00 0.00E*00 0.00 +00 0.00E+00 0.00t+00 e . CM LO! 0.00 E + 00 0.00i+00 0.00!+00 0.00 +00 0 00!*00 0.00 +00 0.00E+00 j INFANT: 0.00E+00 0.005+00 0.00E+00 0.00 +00 0.00!+00 0.00E+00 0.00E+00 0.00.
- 0. 0 0 j ++ 0 "d FOR PATHWAY 2 GtCUNO T. 6 0DY GI-TRACT SONE LIV!R KIONEi THYtDIO l.UN3 SKIN ,
ADULT! 6.62 f + 02 6. 6 2 E+02 6. 62!+ 0 2 6 62f + J2 6 62 E+02 6 6 2 + 02 6.62K+02 T.685+02 1
' YE*N: . 6.6 E+0' 6 42E+04 6.62E+0' !+02 6 62 +0' 6.e21+02 7.64f+02 l CHILD: 66 +0I 6.4 t+02 6 62 +03 o.6 6.a !+02 6 62 +02 s.62 $.a ++ 6.621+02 7.64f+02 ,
& INFANT! 6.62 +02 6 6 !+02 6.6 2 +02 66 i+02 6.o2E+02 6 6 +0 6.62E+02 7.68!+02 ,
FOR PATHWAft V! GETABLE *
'$ T. 80DY GI-TtA*T 20N! LIVER KIDNEY THYADID LUNG SKIN A ULT
- T.42E+ 2.53E+08 00 0.00E+00 jNI 1.2J!+06 07 4.143+0T 4.2 0. 00!+ 00 0.00!*00 0.0gE+00 0.0 0E+0.00E+000.0gt+
00 0.0 0!+ 00 0.00t+ 00 g. 0
- uP!Ei: 8:3i1:83l.00g+:0T:18!83a:8]E+04 01:838:881:888:801:888:881:888:801:880: 881:38 '
; 90R PATHWAY: M!AT i T. SODY GI-TRACT BON! LIVER KIDNEY THYRCID LUNG SKIN
- 1. 6 3 E + 0 5 9.413+05 5.9&E+06 0 00E+ 0 0.00E+09 0. 0 0 + 0 0 0.00E + 0 0 . +00 l A00LTI N2 42*+03 5.30*+03 4.95E+04 0.00$+ 0 0. +00 0.00 +00 0.00E+ . +00 LO .siE+0S 3.53f+05 $7E+0m 0.00!+ 0 0. +00 0.00E*00 0.00E+
t INFANT * .00E+00 0.003+00 9 0. 50e+00 0.00a+00 0.00a+00 0.00a+00 0.00E+ 0 . 8OE+00 0E+00: FCR PAYHWAY COW MILK T. 600Y GI-TAA;T SONE LIVfR KILNEY T4YA0!D LUNG $ KIN DULT8 8.09t+05 4.522+06 2.82f+0T 0.00$+00 0.00!+00 0.00Z+00 0.00E+00 0.00i+00
.E!N! 1 CHILD: . 3.67E+05 49E+C66.355+0e 6.195+361.29E+08 5.20E+0T 0.00!+00 0.00E+00 0 00f+00.0.00E+00 0. 0 0.00!+00 0 5+ 0 0 0.0.00E+00 00E + 0 00.00!+00 0.00!+00 INFANT! T.0!!+06 5.03f+06 2 45E+08 0.00!*00-0.00E+0J 0.00i+00 0.00E+00 0.00!+00 PCR PATHWAY 1 GOA T MILE
- N T. B ODY GI-TRACT SONI LIV!R KIDNEY THYRDID LUNG SKIN-
"ifVh!*
1l!!i: }:jil:82!:!85:891:311:818:!8j*l88:881:88l:88!:l8B:88h:88l: 2: 411:89 i:!! !:8i 1:Iti:818:88E+08 8:881:88 :881:08 8:881:88 :881:88;
' POR PATHWAY: 21HALATION i T. BODY GI-TRACT SONE LIVER " KIDNEY THYROID UNG SKIN
. ADULT: 2.T6E+02 1.1L5+04 9. 4H+03 0.00*+00 0.00t+00 0.00!+00 4.44 +04 0.00{+00:
.:. TEEN! 3.95E+02 1.1H f+04 1. 8 d+04 0.00i+00 0.00E+00 0.00d+ +04 0. 00t+ 0 0 2 CHILO 5.47E+04 5.30!+03 1. O l+04 0.00!+00 0.00t+00 0.00l+00 T.6500 6.84t+06 0. 0 0!+ 0 0 ;
INFANT: 3.62E+02 2.032+03 1.26L+04 0 00E+00 0.00E+00 0.00d+00 6.44E+04 0.00E+00! 3
- ? ,
'k q 1
L r t
'. .. . .. .. , . . . . . . . . . . ~ .
. .-.m ,, + _ , . , -m_. . , . . . , . - , - , , . .
- + .{:. .
. i 3
INDIVIOUAL 00$2 Fo* TOR $ .804 GA3EDU$ !F.8LUENTS -- FOR ISOTOPE
- SR90
/CR PATHWAY! P.UME ADULT 3 T. 800Y GI-TRACT SONE LIV!R K40NEY 1
THYR 0!D LUNG s .TE*N! 0.0)E+00 0.00 0.03E+00 0.00 +00 0.00E+00
+00 0.00i+00 0.00E+00 0.005 $KINi CHILO: 0 038+00 0..J +00 0 00.g+00 0 00 00 0.00E+00 3.00f+00 0.00E+00 0.00!++00 0.00E+00 0.00 +00 i INFANT! +
0.00E+0J 0.00* 00 00 0 00c+00 0.00 +00 <
-' 0.036+00 0 00!+00 0.00$*00 0.00E+00 0.00E+00 0 00l++00 0 00E+000 00E +00 0. 00 0.00E+00
f*]l FOR PATHWAY! Gt0UND ( T. B 004 GI-TRA07 BON! j.
. .AOULT2 L:V!R K!0NEY TdYROIC LUNO t i
'TE!N2 0. 03 E + 00 0. 0 0 !+ 0 0 0. 0 0E + 0 0 0. J0!+ 0 0 0.0 0E+ 00 0. 00400 0.03 8 0 00E+00 0. 0 0 h +K 00I N !
CHILot 0.0)g+00 0.00i+00 0.00E+03 0.00f+00 0.00g*00 00 0.00l+00 0.00E+00 0.008 00
- t .. INFANT: .+00 0.00!+00 0.00!+00 0 008+00 0.00c+ 0.00!+00 0.00E+00 0.00E++00 l 0.0JE*00 FOR PATHWAY: V! GETABLE 9 00!+00 0.00E+00 0.00E+00 0.00E+00 0.00i+00 0 00E+00 0.00E+ l se T. B ODY GI-TRA0T ADULT: EONE LIV!R K:CNEY THYRDIO LU $ KIN, TEiN! 11.3 5 E +10 1 6 3 5+ 09 5. 6 4E +10 0. 0 0i+ 0 0 0.0 E+00 0.00 +00 0.00f+NG 00 0.00 +00
..,CHILO! 2 790) +10 1.54 +09 1 21E+11 0.00 +00 0.0 c 00 0.00 +00 0.00E+00 0.00 +00
- INFANT 4 0 03 +00 + 10 2. 0 4 }* + 0 9 T. 2 T E +13 0. 0 0 + 0 0 0 0 %
- 0. 0 0 + 00 0. 00E + 00 0.00 + 00 ++ 0 0
; PCR PATHWAY: M! A T 0.00!+00 0.00!+00 0.00 +00 0.00!+00 0.00i+00 0.00!+00 0.00!+00 ti T. 60bY GI-TRACT M4 ADulTt 4.458 06 5 j 4 8 + 07 1. 41BON! LIY!R KION!Y THYACID LUNG eTEEN! 2. 93 d ++ 0 s 3tv!+0T E + 09 0. 0 0i+ 00 0. 0 0!+ 00 0. 0 0!+00 0 0 E + 0 0 0. 00 *+SKIN 00
.CHILot 3.8.E+0d 2.34f+JT 1.522+0W 1.1T +0s 3.00s+00 0 00E+00 0.00$+00 0 0 E+00 0.00:+00 jINFANT!
0.00* 00 0.0 0!+ 0 0 0 0 0!+ 00 0.0 f +00 0.00E+ 00
- 0. 0 3 E + 0 0 0. 0 0 3+ 0 0 0. 0 0E + 0 J 0. 0 0 3++ 0 0 0. 0 0 E+ 0 0 FOR PATHWAY: C3W HILA .
40VLT: T. 600Y DI-71ACT 50N! LIV!R KION!Y -THYR 0!O li!N! LUNG SKIN CHILO: 1. 6 7 c +2.70!+Qi 2.23!+09 4.1*t+0) '0 9 1.3T!+08 9.64t+0)
- 6.31E+0)
J.)Ci+Q0 0. 30 !+ 00 0. 0 0.00E*00 0E + 0 0 0. 00!+ 00 0. 0 0E + 0.00* 3NFANT: + . 5 [! + 0 9 3. t s i, 8 1.74
.411+0a 1. 6)3 +13 3. j 0 0+ 0 0 0. 0 0 E+ 0 0 0.00!++00 00 0.00E+00 0.00!+000.00i+00 0.00f+00 FOR PAThWAYi G 3 A T .3I LK
+10 0.w0!+00 0.00E+00 0.002+00 0.00E+00 0.00i+00 I.i T. E00Y GI-T.tA;T t4 ADULT: BON 3 LIVER K:DN!Y THYRDIO LUNG TEEN! .$ KIN CHILO: 3.51E+09 5 0]!,09 4 141+031.0**
3.43:+Qa 1.43f+10 0.00!+00 0.00!+C0 0.00c+00 0.00E+000.00i+00 5.c72+0) 4.tli+v3 j.s!!+10 .003+;0 0.00**00 0.00J+00 0.00!+00 0.00:+0u
+ 10 .j. 30 * + 40 0. 0 0!+ 0 0 0. 0 0i+ 0 0 0 00 E + 0 0 0. 0 0 =+ 00
. INFANT! 9.47c+wi 4 . n 2 + .i n ,.7:e.;) 1. F. +30 20R PAthwart l ih .L.T ; * , 0 00!*00 0 00!*00 0.00E+00 0.00:+00 ADULT: f. auut v . - T .'. A . T 1.vai,0) ' . ti !
. L;V:* *K FliY
.;;4+J6 0.1 4.u. TdYRCIO '.UNG SKIN YEiN1 .
34d+03 0.001+00 2.1':+vs ;...J.J6 * !+e.
'CM4LO
.Nea:4T: i.0 5-Os 4.31d+04 3 420E+0A 0.00i+00 ' .00:+a3
.0 MIO 0.00E++00 0.0 !*09 0.00* 0.o0!+00 00 J.003+00 0.00J+00 10!+05 54;edE+05 00.002+00 003+00 3.011+04 4.;51+33 1 30i+0a i
0.00i+JO 0.002+00 0.00!+00 3t lii+05 0.00i+00 He 1'
.I .
l
- l. ,
e 1 . 4 . . . 6 i
, .m-- , -, -- , - _ - , . , ~ . . - - - - e ,-.
, -. . ...~. .. .._...... ... ...... . _ _ ---
--- --b o a
- 4. p .
p e. g i INDIVI3bAL DD$f FACTDR3 ?OR GAJE3US iPFLUENTS -- POR ISOTCPE : PES 9
^ 'i FOR PATHdAY: PLUME
'[ ADULT:
~
T. SODY GI-7RACT- SONE LIVER K I D ri E Y . TdYROIO LUNG SKIN
..3'. TE!N: . 0.03E+00:0.00!+00 0.03E+00 0.033+000.00E+00.0.00J+00 0.00i+00 0. 0 0!+ 0 00.00E*00 0.00E+00 0.00E+00 0.00E+00
+
. CHILD: - 0. 0 3E + 0 0 ' O. 0 0f + 0 0 0.00E+00=0.00E+00 0.00i+00
'y'# INFANT: . -0. J 0 i+ 0 0 0.005+00-0.00!+00 0.00E+00 0.00E+00 0.00E+00-0.00E+00 0.03E+00 0.00i+00 0.00E+00 0.30d+00 0.00E+00 0.00!+00 0.00E+00 0.00E+00
'$j FOR' PATH,WAY: G40VN3 T. SODY GI-TRACT-
_f
, - ADULT r
- 8. 4E+06 d. SONS LIV!R KIONEf THYR 0:0 LONG- - SKIN TEEN: 8. 45+06-8. 4E+06 8.36d+06-8 34E+0E 3.343+36 8.34E+06 9.30E+06 i CHILD: 4E+06 3. 4E+06.8. 4 E +0 6' S. 34 E+ 3e 8.36E+06 3.345+06 8.34E+06/9.30E+06 INPANT: 8.34E+06 4.J42+06 8 343+0$ 8.34E+06 8.34E+0s 3.34E+06 5. 3 4 E + 0 6 . 9. 4 0 5 + 0 6' 8.34E+06 6.34E+06 8 34E+0o 8.345+06 8.34E+06 8.34t+06 8.34E+06-9.30E+06 POR PATHWAY: V! GETABLE
-8 A00LT: T. 5001.GI-TRACT -90NE LIVER -KION!Y THYROID . LUNG. SKIN
. TEEN: -
- 2. 8 3 E + 0 h 2. 4 4.23E+06'2.525+07'4.75E+06 3 5 + 0 7-- 3.11 E +06 - 7. 3 0!+ 06 0. 0 0 E+ 0 3 0. 00 E+ 00 2. 0 4 E + 0e 0.00i+00.
CHILD: 8. 6 9 E + 06 1. a 2 i+ 0 7 1. 0 ! E + 0 71.11d+07 ,1. 7 5 E+0.00E+00 3 7 0. 0 0 E0.00E+0C.3.50E+06 0.00E+00: INFANT: + 0 0 0.00i+00.5.06E+06 0.00i+00 0.03E+00-0.J0i+GO 0. 0 0E+0 0 0. 0 0t+ 0 0 0. 0 0E+ 0 0 0. 3 0E+ 0 0 0.00 E + 00 0.00i+00; FORP3NMAY: M!AT
)' j ADULT:
T.~SODY GI-TRACT SONE LIVER. KIONEY TdVROID- LUNG SKIN
- T!!N:. 4 29:+06 3.73E+07 4.765+06 1.122+07 0.00E+00 0.00i+00 - '75+06 0 ~. 0 0 i+ -
0 0' CH L3: 3.43E+06 2.101+07 3.90E+0e 4.875+36 0. 0 0E+ 0 0 0. 0 0 5+ 00 1.i SE + 06 0.00i+00
- IN ANT: 5.43E*06 1.1'i+0716.74E+06 1.392+07 0.00E+00 0. 0 0 E + 0 0 ' 3.16 E + 06 - 0. 0 0i+ 0 0
- 0. 03 E +00 0. 3 0!+0 0 0. 0 3E- 10 0. 0 0 5+ 0 0 0. 0 0!+00 0.005+00-0.00E+00 0.00i+00t
[ POR PATHWAY: C3W MILK DULT: i. o0DY GI-TRAOT BONE LIVER KIDNEY THYRDIO( LUNG SKIN
- . (EEN: 4.7)E+05 4 173+D6 5.325+05 1 25 d+ 06 - 0. 0 0i+0 0 0.302+ 00. 3. 49 E + 0E - 0. 0 0!+0 0 CHILO: 8.37E+05 1.74E+06 3.535+06 5.12i+36 2.15E+06 9.23E+05 3. 2.17E+06 48 E+ 360.00E+00 0.00E+00 0.00i+000.003+006.83E+03-0.00E+00 1.01E+06 0.00E+00, INFANT:
' 2.TTi+05 3 352+06 4.0 2E+06 - 7. 02 5+ 0 6 0.0 0E +0 0 0. 002+ 00 2. 075 +0e 0. 00!+ 00 lA FOR PATHWAY: G3AT MILK-
%[ ADULT: T. BODY GI-TRACT BON! LIVER KIONEYi-THYROID LUNG SKIN-TEEN: 6.23E+03 5.42E+04-6 91E+03' .63i604 0.00E+00 1 09E+06 6.6oi+04 1.215+04 .32i+04 0.00!+00 .00i+00-B.88E+03.0.00E+00 .00E+00 4.54E+03 0.005+00
-CHILO:
.INPANT: 2.26E+04 4.71E+04 2.80E+04 6 53t+04 0.00E+00 0.00i+00 1.31E+04 0.00!+00 3 63E+04 4 362+04 5 22E+04 9.12E+04 0.00E+00-0.00i+00.2.70E+04 0.00!+00 FOR PATHWAY: I 4 H A L A T I O.1 T. B ODY GI-TR ACT BONE . LIVER KIDNEY 'TdVRDID ADULT:- LUNG SKIN
' TEEN: 3.35E+02 5.365+03 3.73E+02 8.80E+02.0.00E+00'O.00F+00 3.22E+04 0.00i+00 4.54F+02
'CHIL3: 5.56d+03 5.0$E+02 1 175+03 0.00!+00 0.00!+00 4.84E+04 0.00E+00 INFANT: 5.29E+02-2.24E+03 6.56E+02 .1.062+03'0.00E+00 0.00E+00 4.02E+04 0.005+00
'3.03E+02 7.565+02 4 30E+02 7 .46E+02 0 00E+00 .
0 00E+00 3.22E+04 0.00E+00 1
-4 .
r 1 2 i i i I i
'it O" r'
~
I
- l.
- . I l -{1NDIVIDU AL 0 *S!- F A *....
.............................;.Ai!OU.S T 32
- JI t -- FJR I*0T
!F/LJENT3 ope : ZR95 E
. 0R PATMWAY:'P.UAE .
1-tADULT T. 600Y GI-TRA*T' BCN2- LIVER KIONEY TkYROID LUNG SKIN
*. . t T E I N :
'CHILO: '
- 0. 0)E + 0 0 0.30E+30LO.00E+03-0.00i+00 0.00E+00 0.00!+00 0.00E+00 0.00i+00
,, . I INFANT: 0.03E+00 0.JC3+00 0.00E+00 0.00i+00 0.00E+00 0.003+00 0.00E+03 0.00E+00 O.032*00 '
gM 0. J0 !+ J0. 0. 0 02 + 00. 3 0 0i+ J C 0. 0 3 E+ 0 0 0.00!+00-0.00E+00 0.30E+00 0.03d+00 0.00i+00 0 00i+00.0.00!+00 0 00i+00 0.30i+00 0.00E+00 0.00i+00- g
~
4iPOR~ PATHWAY: Gt C UND. i. T. 5 00Y GI-TAACT. 50NE LIVER K!DNEi- THYROIC j AOULT: LUNG. SKIN TEEN:
; CHILD: 7.43E+06 7..Ei+06 7.43E+06 7.*dE+0e 7.43E+06-7.4si+06 7.48E+06 3.a75+06 7.4 3d +0 67.= 7.3f+36 7.43E+06 4 3 4 7.43E+06
+ 36 7.48E+0s 7.*Si+067.4ai+0e 7.4dE+0s 7.46E+05 7.48i+06 7.4SE+06.8 675+06-iINFANT: 7. Ei+06 7.46E+06 8 375+06
' 7.43E+06 7.463+36 7.4dE+0a 7.483+06 7.4dE+06 7.45E+06 7.4dE+0e 9.673+06 ,
~*
POR PATHWAY: V!GETa5LE '
'd T. BODY'GI-TRACT BONi
- ADULT: LIV 3R KIDNEY THYRCIO LUNG SKIN
- TEEN: 6.45E+03'J.33E+07 2.93E+04 9.55f+^3 1. sue +04 0.00E+00 0.00E+00 0.00i+00
.,i C H I L D : 1.01E+0* 3.375+07 4.63i+04 1.46E 04 2.15E+04 0.00i+00 0.00E+03:0.00E+00 9 INFANT: 2.075+04 L. 33+07'1.06!+05 2.33f+04 3.335+0+ 0.305+00 0.00E+00 0.005+00
- . 0.03E+00 0.00i+JO 0.00i+00 0 075+00 0.00E+00 0.0 0d+ 30 0.00 E+ 00 0. 0 0 E+ 0 0
- t FOR- P ATHW AY:' M! A 7 5
ADULT: T. BC0Y GI-TRACT B3Ni- L*VER FIONEY THYROID' LUNG SKIN TiaN: 7.255+03 3.40!+07 3.34E+04 1.07s+3* 1.63E+04 0.00i+00 0.00E+00 0.00!+00 5.815+03 CHILD: 9.3)E+03 1. H 5+37-2.66E+04 3.455$03 1.24E+04 0.00i+00 0.00E+00 0.00E+00
; 1. 0 'i i + 3 7 4.75E+0+ 1.05f+04 1.50E+0*: 3.00i+00 0.00E+00 0.00E+00
*i.{i INFANT:
0.03E+00 0.00d+00 0.00!+00 0.00d+00 0.00E+00 0.005+00 0.00E+00 0.00i+00 , 704 PATHWAY: C3W MILK s 100LT: T. EC0Y GI-TtA*T 33N1 LIV 3R KILNiy THYR 0!0 LUNG SKIN r/EEN: 3.633+00 1.715+04 1.63E+01 5.40i+JO S.47E+0010.00E+00 0.00E+00 0.30E+00
'C .1I L O : -
.,; INFANT: 6.3)E+00 2.1*i+J4 2.94E+01 9.295+00 1.35E+01 0.00E+00 0.00E+00 0.00E+00s 1 3%5+01 1.573+34 2.13E+01 1.475+046.845+01 1.50i+01 2.15 5+ 01 ' O. 0 0!+ 0 0 0. 00 E + 0 0 ' O. 0 0i+ 0 0
- 1. 21 E + 0 2 2. 9 0 E + 31 3.19E + 01 0. 00d+ 00 0.00E +00 0. 00!+ 00 *
'l FOR PATHWAY: G3A T MILK - '
3 T. B OG Y GI-T.t a
- T' B3NE LIVER KIONEY THYROID C4 ADULT: LUNG
'TEdN: 4.39E-u14 2e35E+03 2.02E+00 6.4 8 5-01 1. 0 2 E+ 0 0 0. 00i+ 0 0, 0. 00 E + 0 0 -0. 0 0 d+SKIN' 00
.CHILO: 7. 6 5 E -01 2.573+03 3 53E+00 1.115+00 1.6*E+00 INFANT: 1.61E+00 1.d85+03'6.20E+00 1 30E+00 2.58E+00 0.00E+00 0.00d+ 0 00.00E+00 0.00 E +000.00E+00 0.00E+00 2.52E+00 1.773+03 1.465+01'3.55E+00 3.83E+00 0.00i+00 0.00E+00 0.00E+00 FOR PATMWAY: I4HALATIO1
'- T. BODY GI-7RACT AQULT: BONE LIVER IIONEY THYRDID LUNG SKIN 7.33 E +0 2 TEEN: 9.99E+02 4. 77 5+ 03 3.40 E +0 3 1. 0 9 8+ 0 3 1. 7 2 E + 0 3 0.00E+00 5.60E+0+ 0.005+00
- CHILO: 4. 72 2+ 0 3 4.6 2 E +0 3 : 1 45 E+ 0 3 2.14 E+ 0 3 0.00i+00 8.52E+04 0.00i+00 INFANT: 1.1TE+03 1. 94 s+ 0 3 6. 02E +03 1.33 E + 03 1. 8 9E+ 0 3 0.00E+00 7.07E+04 0.00E+00 p
- 6.44E+02 6.383+02 3 66E+03 S.63E+02-9.85E+02 0.00!+00 5.55E+04: 0.00i+00 e d
's. t 1 i Ja l
.Q' .,e l
4, 1 L tj Rd \*', b -
k
.e
[! . 0 0 +100
- 0 00+ 900'0 00 +70 0 '0 00 + 300
- 0 00 +?9 0'0 00+ 3 0 0
- 0 00+P C C'0 00+ 3 C0'0 :1NVdNI
- 00 +3 0 0
- 0 00 + 300 *0 00 +7 00 '0 .0 0 +30 0
- 0 - 00 +? O'0'0 00+ 70 0 *0 0 0 +7 0 C *0 0 0+ 3 C0"0 :011H3 '
E00+700*0 00e200*0 00+100*0 00+100'0 00+300*C100+300'0 00+ECO*0 00+3C0*0 : Nill o00 +C0 C '0 : 00 +2 00'0 0 0 +50 0'0 00+300
- 0 .00 *H0 0
- C '0 0+30 0 *0 0 0 +i0 0 *0 00+3CO*0 :1100Y
' NIMS CN01 OIONAHL APN0!1. BIA37 ?NCS 10VH1-10 A009 *1 h0 1V17HhI 1AVMHIVd Mod , 1 0 0 +100 '0 .00 +100 '0 0 0+i0 0 '0 0 0+300 '0 00 +500 *Q 00+30 0 *0 0 0 +3 0 C
- 0 00+3CO*0 :1NVdNI
! 0 0+5 0 0 '0 '0 0+ 3 00 '0 0 0 +10 0 '010 0+3 0 0
- 0 . 0c +G 3 0
- 0 00$3 0 0 '0 0 0 + ? 0 C
- 0 00+3C0'0 :C1IMO
'00+000'0 00 +300'0 0 0 +10 0 *0 0 0+500'0 00 +5 0 0
- C 0 0 + 30 0
- 0 0 0 +F O C *0 00+!C0'0 :N!31
~ 00 +f 00 '0 0 0 + 3 00 '0 00 +iO C '0 - 00+300
- 0 GO+390*0 00+700'0 00+10C*0 00+200'0 - :1100V P'd
-NIMS CNn1 010tAH1 lAINOIN 39AIS INC9 10Vhi-10 ACC9'*1 4 M1TW 1VCD :AYMHavd 80d I'00+200*0 00+?00*0 Oc+100'0 00+300*O?00+900*C 40+300'0 OC+20C*C 00+?CC'0 :1NYdNI.
lCC+100*0 00+ 300 *0'00 +300 *0 C 0 +20 0 '0 00 +300'0 00+300'0 OC+IOC*0 00+3C0'0 :C11H? -
' 00 +7 00 *0 ' 0 0+ 300'0 00+?00'0 00 +*00 *0 00 +CA0
- 0 00+ 5 0 0'0 0 0 +i CC '0 C0+2CO*C : NEE-0 0+10 0
- 0 00 + 300 *0. 0 0 +100
- 0 00+5C 0 '0 0 C+3 5 0 *C C0 + 2 0 0
- 0 O C +F O C
- C C0+300 :11nci
;HIMS CNGT 0104AH1' A3NOI1 UEAIl IN05 10 vel-10 A309 *1 1:
M1IW MCO 1AVPHIVd 80d 00+700*0.00+300'0 00+F00'0 00+700'0 00+300*C 00+300'0 00+FOC*C 00+1C0'0 :1NVdNI~ **. i 0 0 45 0C '0 00 +I00
- 0 0 0+? 0 0 '0 c C 0+100 '0 00 +2 0 0
- C 00+200'0 00+!0C*C C0+500'0 :C1IMO
' 00+300*0 00+300'0 00+!00'0 00+300'0 OC+FOC*C C0+300'0 00+50C*0 C0+200'0 :N331
- 00 +10 C
- 0 0 0 + 300 '0 0 0 +5 0 0 '0 00 +i0 0
- 0 0 0 +1C C
- C 00+!CC'0 OC+FOC*O 00+3CO*0 : 110 0 V . '~.
' NIMS ONn1 OIOhAH1 A3NOIM h!A!1 INCE 10VY1-10 A009 *1 ,
(.1 1YiW : A V P H,1 V d WOd 1 00+!00'0 00 +300 *0 - 00 +T00 *0 00 +100
- O 00+? 0 0'0 0 0+!00
- 0 0 0 +i OC
- O C0+700'0 :1NYdNI .
! 00+i0C'0 = 00+E00'0 00+?00 *0 C0+100'0 00 +700
- C 00+ICO*0 OC+70C*0 00+3C0'0 :C1IH3 _.
00 +iOC *0 = 00+ 300
- 0 00 +70 0 *0 00+i00*0 00+500*C 00+200'0 00+!0C*0 00+200'0 : N 9 31' 00+IOC *O 00+300
- 0 0C+i0 0 *0 00 +300'0 00+500*C 00+5CO*0 00+200*0'00+3CO*0 :1100 V . . . .
r NIMS ONn1 02CHAH1 A3h0IM MEAll FNOS 10 vel-10 AOCG *1 L .- t . .- l 318Y110iA :AYMH1Yd 8 0 d ,.' I 0 0 +?0 0 *0 0 0+ 300
- 0 00 +10 0
- C 0 0 + 20 0 '0 00 +3 00'0 0 0+iC 0 '0 00 +2 00 '0 00+?CO*0 :1NVdMI * *;
00+100*0 00+300*0 00+500*O 00+200*0 00+FOC*C 00+700'0 0C+iOC*C 00+300*0 :C1IW3-00+i00'0 00+300'0'00+500*0 00+3C0'0 00+~00'0 00+!00*0 0C+F00'0 00+9C0'0
- Ni31a. .
00+I00*0 00+300'0 00+100'0 00+900*C OC+100*C 00+I00*0 OC+10C*0 C0+2C0'0 : 110 0 V .' - CHCl 04*tAH1 A,i h 0 I M ' MIAIl ENOS 10VY1-ID A008 *1 l' NIMS , p,, CNn0hD 6
- AVMH1Vd.80dh,*4 d 00+10C*0 00+300'0 00+?00*0 00+100'0 00+?00'0 00+100*0 00+1CC*C 00+300*0 :1MFdNI 00+!0C*0 00+300'0 00+300'0 00+!00*0 00+700*C C0+700'0 00+700*0 00+3C0'0 : C11 H 3 !.*. .
00+300*C 00+300'0 00 4 200 *C :00+ 300
- 0 00+E00*C C0+HCO*C OC+50C*0 00+3CO*0 N331;.'
00+i00*0 00+300*0 00+700*0 C0+900'0 00+700*0 00+iCC*0 00+iOC*0 00+2C0'0' 1110 0 V t. NIMS -CNn1 OIchAH1 A3NQ*) MiAll INCE 10 Val-10 AOC0 *1 .g , 3WA*d :AYMWAVd 30* -. tiffs : ~ 3dOAOSI 3Cd -- $1h201 dI-SnC35VD h 3 d S 301*Vd !S 0 0 1V A01/.!ONI , * ! a .$ *e e?,
^
- M h
+ i i t lINDIVIDUAL 0053 FA; TOR 3'808
.. .. .. .. .. . . .. .. .. .. .. .. .. . . .G A 3 E O U S EFFLUENTS -- FOR 23070*
...............................E : CS134
. . . . . . . . . l
.0R PATHWAY: P.UME :
1AOULT: T. BODY GI-TRACT BONE LIVER KIONEY T'YROIO H
- LUNG SKIN
'- YEdN: 0. 03 E + 0 0.00!+00 0.03E+00 0 0.002+00 0.00E+00 0.00E+00 0. 0 0 E + 0 0. 0. 0 0 E + 0 0 iCHIL3:- 0. 0 0 d + 0 0 3. 0 0 E + 0 0 0. 0 3 5 + 00- 0. 0 0!+ 0 0 - 0. 0 0 E + 0 00.00!+00 INFANT: 0.00i+00
, 0 03E+00 0.00f+00 0.00i+00 0.002+0C 0.00i+03 0.00i+00 0.00E+00 0. 0 0 i + 0 0 ;, i FOR PATHWAY:-Gt0UNO 0.03E+00 0.00i+0C 0.00E+00 0.J0i+00 0.00i+00 0.J0i+00 0.00E+00 0. 0i 0 i+ 00 .
" s t, iADULT: T. 60DY GI-TRACT BON 3' L'1ViR K70N!Y THYROIC
. *i LUN3 m SKINI 4 TEEN: . 2.11E+0i 2 2.115+03-2.11E+03 2.112+08 2.11 E + 0 3 2.115+ 0 s - 2.11E + 0d 2. 465 + 0 3 .! j' CHILD: 11*+03 2.111+062,o32.115+03 2 .11 2.115+03 2 112+0s-2.11E+03 2.115+08 I' 11E+0J 2.11E+08 2.11E+03 2.462+08 jINFANT: 112+0$ 2 115+04 2.11E+0d 2.465+0d*
. 2.11 E + 0 e 2.112 + 0 6 2.11 E + 0 a 2.112 + 0 3 2.115+05 2.115 + 0 3 2 11E + 03 2. 46 5+ 0 8 ',
FOR PATHWAY: V!G3 TABLE '
~
AOULT: BCDY GI-T R A CT BONE ' LIVER KIDNEY- THYRCID LUNG SKIN TEIN: 2.53E+03 5.34f+J6 1.296+0B 3 05f+08 9.8ai+07 d CHIL3: 2.215+06 5.335+0e 2.03E+0s 4.775+0S 1.52E+0s0.005+ 00 3.2 3E +07 0.00i+00
- 0. 0 0i+ 0 0 5. 79 5 + 07 0.00i+00 i i2NFANT:. 1.63E+03 4.105+06 6.63E+0J 7.50f+0d 2.365+0s 0.00!+00 8.462+07 0.00!+00 1 0 00E+00 0.Joi+00 0.00!+00 0.00i+00 0.005+00 0.00i+00 0.00E+00 0.00E+00 i
!FOR P A T'H W A Y : ME A T kN T. B00Y GI-TRACT d ADULT: SONI LIVER KIONEY THYROID LUN3 SKIN
'iTEEN:
, CHILD: 2.33E+07 5.10i+05-1.22E+07 2.31E+07 9.43E+0s 0.00E + 0 0 3 13 E+06 0. 00 E+0 0 1 05E+07 2.353+05 9.74E+0c 2.295+J7 '.235+0s 0.00i+00 2.735+06 0.00E+00 i l INFANT: 5.94E+0s 1.32i+05 1.725+07 2.32E+07 E.73f+05 0.00i+00 3.13E+0e 0.00i+00
- 0. 03 E + 0 0 0.00i+00 0.005+00 0.005+00 0.00E+00 0.00E+00 0 00E+00 0.00i+00 FOR PATHWAY: COW HILK
\DULT: T. B ODY GI-TRACT BCNE LIVER KIONEY THYROI3' LUNG SKIN lisN:
CHILD: 2.05E+01 . 333+J6 1.05f+03 2.503+0i E.115+07 0.00i+00 2.69E+07 0.00i+00 INFANT: _2.03E+0S 5.352+06 1.33d+03 4.30E+08 1.375+03 0.00E+00'5.22E+07 0.003+00 1.45E+08.3.733+06 4 22E+03 6.92i+08 2.14E+03 0.00i+00 T.69E+07 0.00i+00 , 1.23E+03 3.442+06 6.73E+02 1.2Ti+49 3.25E+03 0.00i+00 1.34E+03 0.00i+00
'FCR PATHWAY: G3AT MILK l*4 gj gOU T T. 600Y GI-TRACT BCNE LIV 3R KIDNEY THYROID LUNG SKIN ' I T
CMXLO. 6.1.E+03
.9 + 3 1 .a 32i+07 3.16E+03'7.513+38 2.43E+03.0.00i+00 8.07E+07 0.0 0 E+ 00 4* 3 + 3 1.1 +07
+ T 5.4SE+03
- 1. 1.295+09 4.10E+04 0.00E+00 1.57E+08-0.00!+00 i'
- ' INFANT. .
SE+09 2.J8f+C9 6.43E+03 0.00i+00:2.31E+08 0.00i+00 3.8 6E +03 1.Ja:+07 2.04E+09 3.80E+09-9.73E+08 0 00E+ 00 4. 01E + 0 S 0 00E+00 4 70F PATHWAY: IMH ALAT!04 ~ adult: T. B ODY GI-TR ACT BONE LIVER 'KIONEY -THYROID- LUNG SKIN TEEN: 2. 31 E + 0 4. 3. 3 0 E + 0 2 1.13 E + 04 2.59E+04 9.10E+03 0.00E+00 3.09E+03 0.00E+00 CHILD: 1.74E+04 3.095+02 1.59E+04 3.585+04 1.13E+04 0.00E+00 4.64E+03 0.00i+00 INFANT: T.12E+03 1 22E+02 2.065+04 3.215+04 1.05E+04 0.00i+00:3.84E+03 0.00!+00
!4 2.35E+03 4 23f+01 1 26E+0+ 2.23Ev04 6.04E+03 0.00i+00 2.53E+03 0.00i+00 1 ? *;, - )I !
N , p ' ' o i ,
'k i .g I e
4 d m
ll .a m
e IN0!VIOUAL,D05!' FACT 3R5 FCR GASE003 -!FFLUSNTS -- FOR ISOTOPE : CS146
.)
. R PATHWAY: PLUME T. b ODY GI-TRACT 80N! LIYiR KIDNEY THYROID. LUNG SKIN AOULT: 0. 03 E + 00 0. 0 0!+ 0 0 0. 0 0!+ 00 0. 00!+ 0 0 0.00E+00 0.00i+00 0.00E+00-0.00E+00-
'- TEEN: .
CHILD: 0.03E+00 0.003+00 0.00E+00 0.000+00 0.00E+00 0.005+00 0.00E+00 0.00!+00 INFANT: 0. 0 3E + 00 ~ 0. 0 0 i+ 0 0 0.00E+00'O.00E+00 0.00E+00 0 00i+00 0.00E+00 0. 0 0 i+ 0 0 l 0.03E+00 0.00i+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0 00E+00 0.00f+00 1
- FOR PATHWAY: Gt00NO i T. BODY GI-TRACT- BONE -LIVfR KIONEY I THYRDID- LUNG SKIN A00LT: 4.63E+06 4.60!+06 4.60E+06 6.60i+06 4 60E+06 4.60E+06 4.60!+06 5.215+06 ;
TEEN:- 4.6J E +06 4 60 !+06. 4 6 0E+06 4.60d+06 4.60E+0a 4. = 0 E+ 06 4. 6 0E + 06 5. 21 E+ 0 6 CHILD: 4. 63 E + 0 6 4. 60 3+ 06 4.60E+06 4.60E+06'4.60E+06 4.503+06 4.60E+06 5.21E+06 - I INFANT: *.63E+06 4.603+06 4.60E+06 4.60E+06 4.60E+0h 4. 6 0!+ do 6. 6 0 E + 0 6 5. 21 E+ 0 6 FOR PATHWAY: V! GETABLE T. BODY GI-TRACT BON! . LIVER KIDNEY THYROID LUNG- SKIN
-ADULT: 1. 9 9 E + 06 3.15 E+ 0 5 7. 01 E+0 5 2.772+06 1.54E+0610.00E+00 2.11E+05 0.00E+00 TEEN: 2 14E+06 2.375+05 8.10 E + 0 5 ' 3.19 5 + 0 6 1.74E+06 0.00E+00 2.74E+03 0.00E+00-
' CHILD: 2. 8 J E + 0 5 1. 5 7 5 + 0 5 1.62E+06 4.465+06 2.37E+06 0.00i+00 3.54E+05 0. 0 0i+ 0 0 -
L . INFANT: 0. 03 E + 00 U.00!+00 0. 0 0 5+ 0 0 0.0 0E+ 0 0 0. 0 02+ 00 0.0 0 E+ 0 0 0. 00 E + 00 0. 0 0E+ 0 0 FOR PATHWAY: MfAT T. BODY GI-TRACT BON! LIVER KIONEY THYRDIO LUNG SKIN ADULT: TEEN: 6.53E+055.6 4.74d+05 1 3+05 2.30E+03 9.062+05 5.05E+05-0.00E+00 6.92E+04 0.00f*00 CHILD: 5.53E+05 2., i+04 o+ 04 1.79E+05 7.053+05 3.84E+05.0.00E+00 6.05E+04 0.00i+00-INFANT: 0.03E+00 0.00i+00 5' 095+05 S.5 0f + 0 5 4.53E+05'O.00i+00 6.75E+04 0.00E+00 - 00E+00 0.00E+00 0.00E+00 0.00e+00 0.00E+00 0.00E+00 FOR PATHWAY: C3W MILX T. 300Y GI-TRACT . SONE L VER KIONEYE THYROID LUNG d ULT:
.!N: 1. 4 3 E + 0 7 . 2. 2 6 3+ 06 5.03E+06 1. 9 9 E+ 0 7 ' 1.10 E+ 0 7 0.00Z+00 1.51E+06 0.00 JO CHILD: 2.25E+07 2.715+0e 8.56E+06 3.375+07 1.83E+07 0.00i+00 2.89E+03 0.00 v00 INFANT: 3.64d+07 1.375+06 1.93E+07 5.316+07 2.83E+07 0.00E+00 4 22E+06 0.00E+00 4.14E+07 1.695+06: 3.77E+07 1.11E+08 4.42E+07 0.00i+0019.05E+06 0.00i+00 1
i FOR PATHWAY: G3AT MILK T. BODY GI-TRACT BONE LIVER KIDNEY ' THYROID LUNG SKIN i r AOULT: 1 TE!N: 4.2 7E +07 6.77 3+36 1.51E+07 5.965+07 3.315+07 0.00E+00 4.54E+06 0. 0 0 E+ 0 0 CHILD: 6.73E+07 3.133+06 2.57E+07 1.015+08 5.50E+07 0.002+00 8 67E+06'O.00i+00 INFANT: 1.03E+08 5.60!+06 5.30E+07 1 39E+03 8.49E+07 0.00E+0011.27E+07 0. 0 0 5+ 0 0 1.24E+08 5.062+36 1 13E+03 3.33E+08 1.33E+08 0.003+00 2 71E+07 0.00E+00 : FOR PATHWAY: IMHALATION-T. BODY-GI-TRACT 83Ni LIVER RIDNEY TnVACID.. LUNG SKIN ADULT:
- TEEN: . 3.53E+03 3.70E+02 1.24E+03 4.64E+03 2.71E+03.0.00E+00 3.80E+02'0.00E+00
- CHILD
- . 4.3 4 E + 03 3 e 45 5+ 02 1.6 3 E +0 3 '6 14 E+ 03 3.5 0E + 0 3 0. 0 0E+ 0 0 5.63E + 02 0. 0 0 E+ 0 0 INFANT: 3.
1 63 63 EE +03
+ 03 1. 33 5+0 2 2. 06 E + 03 5.42 E+ 0 3 3. 03E+ 0 3 0. 0 0E+ 0 0. 4 61E+ 0 2 0. 0 0 E + 0 0
- 4. 5 3 2+ 01 1. 5 3 E+03 - 4.26 5+ 03 1. 7 9E+ 0 3 0. 00 E + 0 0 ' 3.73 E + 0 2 0. 0 0 E + 0 0 1
5 l t e a e se s e es e e e o , e e * *9 e
k INDIVIOUAL COS! FAITORS FCR GASEQUS EFFLUfMT5 -- FOR I30 TOPE : C5137 i CA PATHWAY: P'. UME ! I t T. BODY GI-TRACT BONE . LIVER KIONEY TiYROIV AOULT: 0. 0 3 E + 0 0 LUNG SKIH l
*. - TEEN: 0. 0 0 3 0.03E+03 0.30!+00 0.00E+00+ 0 0 0. 0 0E + 00. 0. 00h + 0 0 0.00E+00 0.00!+00 0.00E+00 0.002+00 i' CHILD:
INFANT: 0.00i+00 0.00E+00 0.00!+03 0. 0 0i+ 0 0 0.00E+00:0.00E+00'O.00E+00-0.00E+00
- 0. 0 0i+ 0 0 - 0.0 0E + 0 0 : J. 0 0 E + 0 0 0.00E+00 0.00i+00 t 0.00E+00 0.00i+00 0.00E+00 0.00E+00 0.00E+00 0.00i+00 0.00E+00 0.00i+00 FOR PATHWAY: GROUNO T. 500Y GI-TRACT BONE LIVER A00LT: K!GNEYI THYRDID- LUNG 3 KIN .
-3.93E+03 3.930<03 3.782+08 3.93E+03'3.98E+03 3.93E+0i4 3.98E+08 1,981+08 3.93E+0S 3.9BE+03 4.64d+08 TEEN: 3.33:+0S 3.98E+0e 3.985+08 3.9BE+ 4.A4s+08-i CHILO: t I N F A N T : -- -3.93E+06 3.983*08 3 03E+0s 3.765+08 3.98E+La J.38d+08 J.98E+03 4.o42+0a ,
3.93E+0S 3.982+08 3.93E+08 3.985+08 3.94E+04's.92E+08 1 96E+03 4 645+08 l FOR PATHWAY: V!GETA8LE T. BODY GI-TRACT BONE- LIVfR KIONE) THYRDIC LUNG' A00Li SKIN i TECN '.83E+03 41E+03 5.35d+36'2.10E+03 6.573+06 3.475+03 2. 34.62i+0d 7 5+ 0 8 9.7 1.575 5 E+ 0 7 0.00i+0063.24E+07 03;0.003+00 11d+07 0.00E+000.00E+00 { , CHXL INF Ar '7E+08 4.973+06 8.29E+03 7.365+08 2.59E+03 0.00E+00 9.31E+07 0.00f+00 JE+00 0.00!+00 0.00E+00 0.00i+00 0.00E+00 0.00!+00 0.00E+00 0.00i+00 i
. FCR. PATHWAY: M!AT ADULT:
T. BD0Y GI-TRACT EONE LIVER KICNEY THYROIO LUNG SKIN TEEN: 1.63E+07 4.20J+05 ). 1E+07 2.483+076.82E+05 8.42E+05 0.00i+00 0.00!+00 2.65E+06 2.80E+06 0.00E+00' CHXLJ: 6.93E+06 2.353+35 . 51E+07~;.00!+07 0.00i+00 INFANT: 3.92E+06 1.s63+35 2.775+07 2.o65+07 8.63E+0s 3.005<30 3.11E+06 0.00i+00 2 0.03E+00 0.00i+00 0.00E+00 0.00i+00 0.00E+00 0.00i+00 0.00E+00 0.00i+00 FCR PATHWAY? COW MILK T. BODY GI-TRACT SONE LIViR- KICMEY TdVROIO LUNG SKIN C U LT .* E5N: 1.3SE*03 4.573+06-1.54E+03 2.10i+08'7.13E+07 0.00E+00 2.37E+07 0.00i+00 CHILJ: 1.29E406 5.173+36 2 7sE+03 3.705+08 1.26E+04 0.00i+00 4.90E+07 0.00i+00 ; I N F '.N T : 9.43E+07 4.02i+06 6.71E+03's.42E+03'2.03f+03:0.00i+00'7.53E+07 0.00i+00 ' 8.83E+07 3.323+06 1.071+09 1.25E+09 3.36E+03 0.00i+00 1.36E+03 0.00i+00 , FPW FATHWAY: G3AT MILK I T. B ODY GI-TR ACT SONE LIVER K!ONEY THYRDID
- ADULT: 4.13E+08=1.22i+07 4 61E+03 6.30E+03 2 14E+03 0. 00 i+ 0 0 7.11E + 07 - 0. 0 0 E+
LUNG SKIN i
. TEEN:
- 3. 8 7 E +0S 00 CHILO: 2.8%E+0$ 1. 5 8 5+ 07 8.35E+03 1.115+09 3.785+0s 0.00E+00 1.47E+03 0.00E+00 '
INFANT: 1.21d+07.2.01E+09 1. 93 f + 0 9 4.2 d E+ A 8 0.00i+00 2.26E+03 0.00E+00 ,
- 2. 6 5 E +0 3 1.14 3+ 0 7 3.21 E+0 9 3.76 E+ 09 1. 01E+ 0 9 0.00E+00 4.09E+03 0.00E+00 '
POR PATHWAY: IMHALATION T. BODY GI-TRACT' BONE LIVER RIDNEY T4YROIO LUNG SKIN ADULT: ' . TEEN: 1.35E+04 2.562+02 1.52E+04 1.975+04 7.05E+03 0.00E+00 2.38E+03 0.00E+00 CHILO: 9.87E+03 2.595+02 2.13E+04 2.695+04 9.64E+03 0.00i+00 3.83E+03 0.00E+00 INFANT: 4.07E+03
+ 1.133+02.2.870+04 2 62E+04 8.95E+03 0.00E+00 3 30E+03 0.00E+00-1.4'E+03 4.23E+01 1.74E+04 1 94E+04 5.46h+03 0 00E+00 2.26E+03 0.00E+00 1
I' I L 1
.~
-a
'b o I
t^. ~ INDIVIOUAL 005! FA; TOR $ P04 GASE:US 2P7LUENT3 -- POR ISOTCPE : BA140 sR PATHWAY: PLUME T. 800Y GI-TRACT BONE LIVER K!CMET THtROIO LUNG SK!N !
. ADULT:
. TE8N: 0.03E*00 0.00!+00 0.00E+00 0.0 3 E r 00: 0.3 0 !+10 0.00: 0.00i+JO 0.00E+001 0 00E*00 0 00E+00 0. 0 0 5+ 0 0 1 i CHILO: 0.03E+00 0.00i+30 0.00E++00 0.00E+000.00E 00 3.30i+00 0 00E.+00~0.00E+00 0.00E+000.00i+00 00 0.00a+00 0.00E+00 0.00!+00 J INFANT:
l 0.036+00 0 00!+00 0.00E+00 0 00i+00 0.00E+00 0.00!+00 0.00E+00 0.00E+00 FCR PATHWAY: G40LNO T. BOCY GI-TRACT 10NE L;VER KICNEY' T M Y R O I D- L URG ' SKIN ADULT: 6.27E+05 6.27!+05 6. 2 7 E s 5 6.27-+05 6.27E+05 6.275+05 6 27E+05 7.16 ! + 0 5 4
*-TEEN: 6.275+05 6.27!+05 6.
CHILD: + 0 5' 6 2 7 6.272+05 6 27E+05 7.16 2+ 0 i ;<l 6.27E+05 e. 2 7 3+ ]S 6. .(7 E + 0 s.275+35 75+05 5 - 6. 27 3 6.273+05.6 5273+05
+ 0 5 6.272+05 7.163+05-
- - INFANT: 6.27E+05 6 175+05 6.27E+05 6.276+05 6 27E+05 6.275+05 6 27E+05 7.165+05 )
- FOR PATHWAY: V! GETABLE '
i l- T. 6 00Y GI-TR&;T SONE LIV 2R KIONEY THYRO 0 ADULT: - LUNG SKIN
- TEEN: 1.35E+05 4.295+06'2.085+03 2.625+03 8.39E+02 0 00!+ 00 1.50E+03 0. 0 0 i+ 0 0 1 CHILO: 1.62i+05 3.385+06 2.52E+06 3.096+03'1.05E+0J 0.00i+00 2.07E+03 - 0. 0 0 i+ 0 0 INFANT: 3.13E+05 2.723+J6 5.36E+06 4.s95+03-1.53E+0J 0.00!+00 2.80E+03 0.00!+00 0.03 E +00 - 0.0 0 4 t J O 0 00E+00 0.00i+00 0.00E+00 0.00!+00 0.00E+00 0.00i+00:
FOR PATHWAY: MEAT T. - B ODY GI-TRACT BONI LIVER: K:D'1E Y THYROIO LUNG - SKINi ADULT: 3.615+04 1.13 5 + 0 6 : 5. 5 3 E + 0 5 6.915+02 .35E+02 0.002+00 3. 96E + 02 , 0,0 0i+ 0 0 Ti5N 2.93E+0+ 7.00!+05 6 55E+05 5.585+02 1.8)E+02 0.00E+00 3.75E+02 0.00i+00 , CHILD: 4.93E+04 4.15:+J5 8.40i+05 7.365+02 2.40E+02-0 00i+00 4.39E+0Z 0.00i+00 ' INFANT: 0.03E+00 0.30!+00 0.00E+00-0.00i+00 0.00E+00 0.00i+00 0.00E+00-0.00i+00 FCR PATHWAY: C3W HILK i T. 800Y OI-TRA7 SCN! LIVER. K;CNEY TdVR3:0 LUNG SKIN
'ULTi
.EN: 3.376+04 1.063+06 5.15d+05-6.475+02 2.235+02'0.00!+00 3.T0E+02 0.00i+JO uMILO: 5.995+04 1. 43 f + 0 6. 9. 2 9 E + 0 6 : 1 14 E+ 0 3 5.36E+02 0.00!+00.7.66E+02 0.00i+00 INFANT: 1.31E+05 1.143+36 2.24E+06'1.175+03 6.40E+ 02 : 0. 0 0i+ 0 0 :1.17 E+ 03 0.00i+00 2.35E+05 1.133+06 4.62E+06 6.62i+03.1.10E+04 0.00E+30 2 83E+03 0.002+00' FOR PATHWAY: G3A T MILK T. B ODY GI-TRACT BONE LIVER KIONEY .THYROIO LUNG SKIN
- ADULT:
TEEN: 4.05E+03 1.275+05 6.13E+04 7. 7 6 5 + 01- 2. 64 E+ 01 - 0. 0 0E+ 0 0 s 4.44 E + 01 0.00i+00 CHILD: 7.13E+03 1.72i+05 1.12E+05 . 372+02.6.63E+01 0.00c+00'9.19E+01:0.00E+00 i w INFANT: 1 575+04 1.365+05 2.85E+04 1.365+05 2.69E+05 5.54E+05 2.365+02:7.6dE+01 5.542+02 1.32E+020.J0d+00 1.41E+02.0.00i+00-, 0.00!+00.3.40E+02'0.00i+00 + FCR PATHWAY: IVHALATION ! T. B ODY GI-TRACT BON! LIVER KTONEY THYROIO LUNG SKIN ADULT: TEEN: 8.14E+01 6.92i+03 1.24E+03 1.55s+00'5.30E-01?0.00E+00 4.03E+04 0.00E+00 CHILD: 1.12i+02 7.253+03 1.73E+03 2.13E+00.7.23E-01 0.00!+ 0 0 6 44E +0 4 ' 0. 00 E+ 00 INFANT: 1.375+02 3.235+03 2.35E+03:2 05E+00 6.70E-0110.00E+00 5.52E+04'0.00E+00 9.19E+01 1 22i+a3 1.78E+03 1 785+00 4.2oE-01LO.00!+00 5.06E+04 0.00i+00 i e w a m/ .
)
A. , , r IN0!/ IOU AL 003! - F ACT OR3 POR ' 5 A550U3 EFFLUENT S -- FOR - 150Tod! : C1141
.JR' PATHWAY: P '. U M E i T. BODY GI-TRACT' . BONE . LIVER KIDNEY TdY20I0 LUNG SKIN :
ADULT: 0.03E+00 0.30i+00 0. 0 0E + 0 J - 3. 0 0i+ 00 0. 0 0 E+ 00 0.0 0!+ 0 0 0.00E+00 0.00E+00 &
'LTE!N: 0.03E+00 0.303+30.0.00i+0J 0.00i+00 C.00E+00 0.00:+00 0.00E+00 0.00i+00 *1 i CHILD: 0.03E+00 0.30!+00 0. 0 0 E + 0 3 0. J 0 3+ 0 0' 0. 0 0 E + 0 0 - 3. 0 0i+ 0 0 0.00E+00 0.00i+00 t INFANT:
0 03E+00 0.00i+0C 0.00E+00 3.00E+00 0.00E+00 0.00i+00:0.00E+00 0.00!+00 ) e I 70R PATHWAY: G10 UNO a s- > T. E00Y GI-TRACT 3DNf LIVER KICNEY' T n T R D I an - LUNp. SKIN'I ADULT: 4.17 E + 0 5. 4 17 3+ J 5 4 17 2 + 0 5 4.17 5+ 0 5 4 17 5,0 5 4.175+05 4.17E+05 4.70E+05 ' TEEN: 4.17E+05-4 173+05 4.17 5 + 0 5 4.17 5+ 0 3. 4.17 E + 0 5 4 175+05 4.17E+05 4. 7 0 E+ 0 5 . ;: CHXLO: 4.17 E + 0 5 4.17 5 + 0 5 . 4.17 E + 0 5 4 17 5 + 0 5 4.17E*05 4.17E+05 4.17E+05 4270f+05, INFANT: 4 17E+05 4.175+0i 4.17 E,0 5 ' 4.17 5 + 0 5 4.17 E + C p 4.17s+05 4.17E+05 4.70E+05 , FOR' PATHWAY: V!G ET A B L i- I j T.-B00Y GI-TRACT B3Ni LIVER KIONEY TMYRDIO; LUNG- SKIN AGULT: 3. 5 3 E + 0 2 1. 2 0 i + 0 7 4. 6 3 E + 0 3 3.13 E+ 0 3 1. 4 5 E + 0 3 0.00i+00 0.00E+00 0.00i+00-TEEN: 5.57E+02 1.393+37 7.2 6 E + 0 3 4.d 5 E + 0 3 2. 2 5 E+ 0 3 0.00i+00 0.00E+00 0.00E+00 CHILD: - 1. 2 3 E + 0 3 1. 0 8 2+ 0 T 1. 7 4 E + 0 4 3. 6 7 5+ 0 3 3. 8 0i + 0 3 3. 00i+ 00 0. 00 E + 0 0 0.00!+00 ;j
. INFANT: 0.0Ji+00-0.G0i+00 0. 0 0 E+00 0.0 0i+ 0 0 0. 0 0E+ 00 0.00d+00-0.00E+00.0.00i+00 :
FOR PATHWAY: M! A T T. BODY GI-TIACT SONE LIVER KIDNEY' THYROIO LUNG SKIN ' ADULT: 1.95E+01 6.563+35 2.54E+02 1.T22+02 7.97E+01n0.00i+00 0.00E+00 0.00E+00 e TE5N: 1. 6 3 E + 01 4.375+35 2.13 f + 0 2 . 4 2i+ J 2 6. 7 0 E + 01 0. 0 0i+ 0 0 0.00E+00 0.00i+00' CHILO: 2.97E+01 2.30i+05 4.01E+02 2.00i+02 S.77E+01 0.00!+00 0.00E+00 0.00E+00 INFANT: 0.03E+00 0.00i+0C 0 00E *00 3.30i+ 00 0.0 0i+00 0.00i+00 0.00E+00 0.00i+00 .
'OR PATHWAY: C3W HILA T. 600Y GI-TRACT ECNi LIVER" KIDNIY- THYR 0!3 LUNG SKIN SULT:
6.71E+00 2.165+05 8.75E+01 5. 9 2 i+ 31 2. 7 5 E+ 01 3.30E+00 0.00E+00 0.00i+00
- i Eih:
CHILD: 1.23E+01 3.365+05 1.60i+02 1.375+02 5.04E+01 0.00i+30 0.00i+00 0.00i+00 ! INFANT: 2.93E+01 2.465+05 3.95E+02 1.975+02 S.64E+01 0.003+ J0 0.00E+00 0.00i+00 li 5.62E+01 2.475+35 7. 8 3 E+ 0 2 4. 73 5+ 0 2 1.4 7 5+ 0 2 0. 0 0i+ 0 0 0. 00 E + 0 0 0. 0 0 i+ 0 0 'l 1 FOR PATHWAY: G3AT MTLK 4 e T. 800Y GI-TRACT SONE LIVER KIONEY TdYROIO LUNG' 5 KIN
' - AOULT:
- TEEN:
8.05E-01 2.723+04 1.05E+01 7.10i+00 3.30E+00 0.00E+00 0.00E+00 0.00i+00
' CHIL3:
1 43E+00 3.53f+04 1.93E+01 1. 2 9 5 + 01 6.05E+00 0.00i+00 0.00E+00 0.00i+00 3.51E +00 2.955+04 4.74E+01 2. 3 71+ 01 1. 0 4E+ 01 0.00E+00 0.00E+00 0.30E+00 IN' ANT: 6.75E+03 2.965+04 9.4 0 E + 01 5. 73 E+ 01 1.7 7 E+ 01 0.00E+00 0.00E+00 0.00i+00 POR PATHWAY: IMHALATION
- T. 8 00Y GI-TRACT BOME LIVER = KIDNEY THYR 3ID LUN3 - SKIN ADULT:
- 4. 8 4 E + 01 3. 3 0 i+ 0 3 6. 31 E + 0 2 4. 2 3 E+ 0 2 - 1. 9 ? E + 0 2 0.00i+00 1.15E+04 0.00E+00 TEEN:- 6.67E+01 4.01E+03 9. 0 0 E + 02 6 01 E+ 0 2 ' 2. 81 E + 0 2 0 005+00 1.95E+04 0.00E+00
- CHILO: 9.13E+01 1. 7 9 5+0 3 1. 24 E +03 6.196+ 0 2 2.71E+ 02 0. 00i+00 1.72E+04-0.00E+00 INFANT: 6 33E+01 6.33f+02 8.7 9E+02 5.28 2+ 02 1 66E+0 2 0.005+00 1 64E+04 0.00E+00 g
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- 9 p INDIVIOUAL 0051 PA TORS FOR GA3EOUS 2FFLUESTS -- FOR ISOTDPE
! ? C3144
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'JR PAfMWAY: P.U M E L, '
T. BODY GI-TRACT BONE LIVER' KIONEY THYR 010 (UNG SKIN + 0.03E+00 0.30i+00 0.00!+00 0.00!+00'0.00E+03 0.0Ci+00 0.00E+00 0.00i+001 J ADULT:- TiEN: 0.03E+C0 C.30i+00 0.00E+00 0.00!+00 0. 0 05 0 3. 0.0 0!+ 00 0.00E+00 0.00d+00 , CHILO: 0.0):+00 0.J0i+00 0.00E+03 3.J0i+30 0.00!+00 0.000+30 0.00E+00 l JNFANT: 0.03E+00 0.305+00 0.00i+00 0.00i+00 0.00E,00 0.003+00-0.00E*00 0.00i+00
- 0. 3 0 d+ 0 0 1
.--FOR PATHWAY: GICUNO , .
T. BODY SI-TRACT SON! LIVER K I O.12 Y' THYROI2 LUNo- - SKIN 1 J. - ADULT: 2.12E+06 2.12i+06-2.12E+C6 2.12i+0e 1.12E+06 2.12i+ 0 6 . 2.12 E + 0 6 2.45E+06-) TEiN: 2.1)E+0s 2.12i+06 2.12E+0e 2.12 i+ 0 2.12E+06 6 2.12E+03 2.12i+06.2.12E+06 2.12i+06 {.455+06.- CHILD: .lfE+0a 2.125+06 2 12i+36 2.12i+06 2.12E+36 INFANT:- .12i+06 2.12i+06 2.12E+00'2.122+06 2.12E+0a 2.12 2+ 3 6 2.12 E + 0 6 - 2 .45 451+06'.1 5+ 0 6 t FOR PATHWAY: V! GETABLE L L' T. 600Y GI-T1ACT B3NE~ L VER KIDNEY THYRDIC LUNG SKIN-A00LT: 4.63E+04
. TEEN: T.73E+04 2.915+08 8.62E+05 3.60 3.}2f+03 1.44E+0e +05.2.14E+03 5.952+33 3.562+050.00E+30 0.00E+03-0.00E+00'H 0.00i+00.0.00E+00 0.00i+00 , CHIL3:
INFANT: 1.375+03 2.s73+03 3.51E+06 1.10 i+ 3 6 6.10E+05 0.00E+00 0 00E+004 0.00!+00 l 0.03E+00.0.30f+00 0.00E+00 0.00!+00 0.00i+00 0.003+00~0.00E+00 0.00!+00 '
.FOR PATHWAY: H!AT T. 83DY-GI-TRACT. 60k! LIV!R KICNEY' THYROID LUNG SKIN.'
l' ADULT: 1.41E+03:3.90!+06 2.63E+04 1 10E+J4 .53E+03 0. 00 E+ 00 0.00E + 00 0. 0 0i+ 00 t TE N: 1.1)!+03 5.33d+36 2.2)E+04 9.185+03 a.43E+0* 0.30E+00.0.00E+00 0.00!+00 l .CH LD: '2 23E+03 3.42d+06-4.IIE+04 1.311+3+ T.24E+03 0.00!+00.0.00E+00 0.00i+00 L: INFANT: '0.03E+03 0.30!+00 0.00E+0 0 0.J0E+ 00 C.00E +0 0 - 0 00i+ 00 0.00E +00 0.00E+ 00 , FCR PATH 4AY: C]W MILK T. SODY 31-TRACT BONE LIVIR K*DNEY THYROID LUN3 SKIN. SULT: 3.47E+02 2.13f+06 6.46E+03 2.70i+03 1.60E+03 0.00J+00 0.00E+00 0.00i+00 45N 6.39E+02 2.995+06 1 19E+04 4.92i+03 2.94E+03 0.00!+00 0.00E+00 0.005+00-JniiU: 1.562+03 2.40i+06 2.93E+04-9 19:+03 5.09E+02 0.30!+00.0.00E+00-0 00E+00 ' INFANT: 2.35E+03 2.415+36 4.20E+0* 1.T2E+04 6.93E+03 0.00i+00 0.00E+00 0.00i+001 FOR PATHWAY: G3AT MILK , T. BODY GI-TRACT BON! LIVER KIONEY THYRCID - LUNG SKI'Nw 4.15E+01 2.52i+05 T.T5E+02 3.243+02 1.92E+02 0.00i+30 0.00E+00 0.00E+00 ' AOULT:: TEEN: T. 6 7 E + 01 3. 5 9 5+ 05 1. 4 3 E +0 3 5.9 0 E+ 0 2 3.5 3 E+ 0 2 - 0. 0 0!+ 0 0 : 0. 00E + 0 0 0. 0 0!+ 0 0 CHILD: 1.83E+02 2. 3 3 5 + 3 5 - 3. 5 2 E + 0 3 .1.10 i + 3 3 6.11 E + 0 2 0.00i+00 0.00E+00 0.00i+00 INFANT: 2.8;E+02 2.395+05 5.04E+03 2.06E+03 8.24E+02 0.00i+00 0.00E+00 0.00i+00 " FOR PATHWAY: IMHALATION T. BODY GI-TRACT' BON! LIVER %IONEY THYROID LUNG SKINL ADULT:- 5.83E+03 2.395+04 1. 09E+ 05 4.54 E + 04 2.69E+04 0.00E+00 2.46E+05 0.00!+00 4 TEEN: 8.32E+03 2.745+04 1.55E+05 6 425+04 3.83E+04 0.00E+00 4.24E+05.0.00E+00 l CHILO: 1.15E+04 1.235+04 2.15 E + 0 5 6.T 15 + 04 3.T2E+04 0.00E+00 3.T9E+05.0.00i+00
.INPANT: 5.53E+03 4.T02+03 1.015+05 3 84E+04 1.T0E+04 0.00E+00 3.12i+05 0.00E+00 a
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4 i . lt INDIVIOUALL 00$$ ' F ACTOR 3 FOR < G A3EOUS' !F8LUENTS -- FOR-ISOT0*E : .1131 -! eCR PATHWAY: .P '. U N E i . T. B ODY: GI-TRACT-. I BONI 4' AOULT: -LIV!R- KIONET TdTR0!-D LONG' 3 KIN-
- 0. 03E + 00
,% TEEN: 0. 0 0 !+ 0 0 0.00E+00 0.00E+00 0.00E+00 0.00i+00 0.00E+00 0.00!+00 '
! CHILO: 0.03E+00-0.30i+00 0.005+00'O.00E+00 0.00E+00 0.00i+00 0.00E+00 0.00i+ 00 '
INFANT: 0 03E+00 0.00i+00 0.00E+00 3.00i+00 0.00i+00 0.00!+00 0.00E+00 0. 0 0i+ 0 0 l' 0.03E+00 0 003+00.0.00E+00^0.00i+00 0.00E+00 0.00i+00 0 00E+00-0.00E+00 6 7 FCR PATMWAY: GRO UND : T. B CCY- GI-T R ACT BONE IVER KIONEY T.1 Y R C IC - $ KIN ' i A00LT: -2.63E+05c2.533+35 2.63E+05 LUNG TEEN: 33+05 2.63E+0D 2 433+05 2.63E+05 J.195+05 ' CHILO: 2.63E+05 2.633+05 2.63E+05-2 2.c3E+0S 1.635+05 533+05 2.63E+05 . 63E+05-2 63E+052.2.a3E+05.2.63E+05 2.63E,03 63 5+ 0 5 2.63E+05'3.195+05 3.19E+05 INFANT: J' 2.63E +05 2.33 5+05 2.63 E t 25 2.635+05 2.63E+05 2.635+05 2.63E+05 3.195+05- l POR P A THWAY: V!G ET13LE l
-ADULT:
T. EDDY GI-TRACT EON! LIVER KIONEY THYROID' - LUNG. SKIN i TEiN: 4.43E+05 1.342+05 5.41 E + 0 5 7.7* E+ 0 5 '1.3 3 E+ 0 5 : 2 54 E + 0 B 0.00E+00 0.00!+00 j CHILO: 4.02E+05
- 5. 8 3 E + 0 51.453+05 9.13 3 + 0 45.353+05 1.02E+06 7.4d5+05 1 295+0s 2.laE+02 0.00E+00 0.00E+00 1.035+06'1.63E+0a 3.395+03.0.00E+00 0.00!+00
-INFANT: -!
0.03E+00 0.J0i+00 0 00i+00 0.005+00 0.00E+00-0.00i+00 0 00E+00.0.00i+00 I FOR PATHWAY: M!AT h T. BODY GI-TRACT BnNi LIVER- KIDNEY THYACID LVNG SKIN' l ADULT 8.73E+04'4.015+04 1.0$E405 1.525+05 2.60E*05 4.36i+07 0.00E+00 0.00E+00 TEEN:
; CMXLD: 6 64E+04 2.445+04 8.32E+0 1.24f+05 2.13E+05 3.505+0? 0.00E+00 0.30i+00 '
INFANT: S.35E+04 0.0JE+00 0.00i+001.465+0401.64E+05 1.65E+05.2.70i+05 5.443+07 00E+00 0.005+00.0.00E+00 0.00i+00;00.00E+00 00E+00 0.00!+000.00!+00-FOR PATHWAY: C3W MILK I T. B ODY GI-TRA;T EON! LIVIR. KIONEY THY R !D. OULT: LUNG SKIN g (E!N:- 2.3)E+06 1.10!+0e 2.92i+06'4.17E+06 T.16h+06 1.375+39 0.00E+00 0.00!+00 CHILO: 3.95E+05 1.473+06 5.30!+06 7.42E+06 1.2 8 E + 0 7- 2.161+ 0 9 0.00E+00-0.00i+00 INFANT: 7.34f+06 1.155+06 1.29E+07 1.29E+07-2.12E+07 4.275+09 0.00!+00 0. 0 0i+ 0 0
- 1. 3 3 E + 0 7 1.133+0e 2. 6 3 E +0 7 3.16 E + 0T 3.6 9 E+ 0 7 1.04 E +10 0. 00 E + 0 0 0.00E+00- ,
FCR PATHWAY: G3AT MILK I T.'600Y GI-T R A CT BON 3 LIVER KIDNEY THYRCID LUNG SKIN-ADULT: TE5N: 2. 8 7E + 0 5 1.32i+06 3.50i+06 5.012+06 8.59E+06 1.34E+09 0.00E+00 0. 0 0 E+ 0 0 CHILD:- 4.73E+06 1.763+06 6.36E+06!d.90i+06:1.53E+07--2 50i+09 0.00E+00 0.00E+00 INFANT: 8. 81 E +016 355+06 1.672+07 1. 3 81+06 1 54E+0F 1.55E+0712 3.22E+07,3.79E+07: 55E+07 4.43E+07 5.135+090.00i+00 1.253+10 0.00E+00=0.00E+0C
- 0. 0 0 E+ 0 0 FOR PATHWAY: I1HALATION T. BODY GI-TRACT SONE LIVER *KICNEY THYROID LUNG $ KIN ADULT:
TEEN: 6.49E+02 1.995+02 T 99E+02 1.13E+03 1.94E+03 3.78E+05 0.00E+00 0.00!+00 CHILO: . 8.64E b .37 E+02 + 029.015+01
- 2. 06 5+02- 1 12 E+ 03 1. 565+ 03 2.6 6E+ 03 4.64 f+0 5 0.00E +00 0. 0 0 E+ 0 0 INFANT: 1. 5 2 E+0 3 1. 5 2 E+ 03 2.5 0 E+ 03 5.15 E+ 05 0. 0 0E +0 0 0.00E+00
- 6. 21 E + 0 2 3. 3 6 2 + 01 1.20E+03 1.412+03 1.64E+03 4.70i+05 0.00E+00 0.00E+00 l
h
- - -. - - - . .- -.- ~ -. - . - . -
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FOR IJOT OP El : 2133 l
- INDIVIDUAL-
. . - - . . . . . . 005.!1 - - - -F- ACTORS
- - . . . . - -!PCR
- - - - GASEQUS
- - - . . . - - - EF8LUENT
- - - - - - - - .S . .-. . . . . - - - - - - - - - - . . . ,
1
.JR. PATHWAY: P.UME i l
T. 500f GI-TRACT EDNi LIVER. KIONEf~ THY ROIO. - . LUH3 SKIN ADULT: ' O.03E+00 0.30i+00 0.00E+00 0.00f+00 0.00E+00 0.00E+00'O.00E.00 0.003+00 '
<V TEEN: 0.03E+00 0.30!+00 0.00E+00 0.00E+DO 0.00E+00 0.00i+00 0.00E+00'O.005+00
- 3.03f+00 0.00E+00 0. 0 0E +0 0: 0.00!+ 00 0.00i+00'O.00i+00 0. 0 3 5 + 0 J. 3. 0 0 ~:+ 0 0 CHILO:
LINFANT - 0.03E+00 0.00!+00 0 00E+00 0.00!+00 0.00E+0-' O.00E+30.0.00i+03 0.J0i+00 FCRtPATHWAY: GROUND
- T. B ODY GI-TRACT B3Ni LIV!R KIONEYS TdVROIa LJNS 3 KIN 3.7 5 E +043.755+04 3.73f+04 3.75E+04 3. 7 5 5+ 0
- 3.73 E + t.
AOULT:
- TEEN: 3.75E+04 3.75s+043.755+34 3.755+04 3.7 3 E + 0 3.755+04 3.75E+04 3.755,04 . *.563+04 4. 56i+ 04 r.
CHILO: 3.75E+06'3.7ti+04-3.7;E+04 3.751+04 3.75E+04 3.755+04 3.75E+0* 4.565+04 , 3.75E+04 3.75d+34 3.7aE+04 3.75E+04 3.75E+04 3.755+04 3.73E+04 4.565+04
- INFANT:
FOR PATHWAY:- V!G ET ABLE T. 8 0DY GI-TRACT BONE LIVER; KIONEf 'TnYRDID LUNG SKIN 1'- l: -ADULT: ~ 7.07E+03 2.33E+04-1.33E+04 2.325+04'4.05E+04 3.415+06 0.00E+0] 0.30!+00
-TEEN 6.415+03-1.595+04 1.26E+04 2.10i+34 3.63E+04 2.93E+36 0.00i+00 0.00i+00 0. 0 0 i+ 0 0 CHILO: 1. 0 $ E + 0 4 1.13 3 + 3 4 2.26E+04 2.795+04'4.65E+04'5.195+06 0.00E+00
- 0. 03 E + C 0 0. J0 i+0 0 - 0. 0 0i+0 0 . 0. 00 s+ 0 0 0. 0 0E+ 00 0 0 01+ 0 0 0. 00 s + 0 0j o . 30i+ 0 0 INFANT:
FOR PATH'WAY: H3AT j T.' BODY GI-TRACT EONE . LIVER KICNEY THYR 0!D- lum 3 - SKIN ADULT: 2.01E-03 5.733-01 3.79E-03 6.605-03 1 15E-02 3.705-01 0.00E+00 0.00i+00 TEEN: 1.64 6-03 +. 0 7 5-05 3.17 E-03 5. 3 ai-0 3 9.
- 4 E-0 3 7. 5 2 3- 01 0.00E+03 3.00i+00 CHILO: 2.75E-03 2.345-03 5.90E-03-7. 1.22E-02-1.352+00 0.00i+00 0.30i+001 ,
INFANT: 0.00E+03 0.30i+00-0.00i+00 0.495-03 00!+00 0.00E+00 1s '92+00 0.00E+03 0.30i+00 FCR PATHWAY: C3W HILA T. 5 0DY ' GI-T R ACT 23NI . LIV!R- KIONEY TM. ACID LUNG 3 KIN i SULT: 2.075+04 4.12i+04 3.915+04 6.315+04 1.19E+05 1.00!+07 0.00i+0J 0. 0 0 i+ 0 0 l idN: 3.73E+04 9.173+34 7.15E+04 1.215+05 2.13 E + 0 5 1. 6 9 5 + 0 7 0.00E+00.0.J0i+00 CHILD: 8.12E+04 8.525+04 1.74E+05 2.155+05 3 53E+05 3.99E+07 0.00i+00 0.00!+00 :
- INFANT: - 1.f5E+05 9.335+04 3.67h+05'3.34E+05 6.28E+05 9.712+07 0.00E+00 0.00i+00 1
FOR PATHWAY: G3AT MILK T. 8 00Y CI-TR ACT EDN! LIVER KIDNEY- TdVROID. LUNJ SKIN-ADULT: 2.49E+04 7.343+04 4.69E+04 $.175+04 1.42E+05 1.20E+07 0.00E+00 0.30E+00 TEEN: 4.44E+04 1.10E+05 8.57E+04'1.45E+05'2 55E+05 2.03E+07 0.00E+00 0.00E+00 CHILD: 9.75E+04 1.34f+05 2.0 S E +0 5 2. 38 E+ 03 4.2 9E+ 0 5 J 4.7 9 2+ 07 0.00 E + 00 0.00E+00 INFANT: 1.83E+05 1.382+05 4.40E+05 6 41E+05 7.53E+05.1.165+08 0.00E+00 0.00s+00 FOR PATHWAY: IMHALATIC1 T. BODY GI-TRACT BONE LIVER KIONEY TMY ROID .. LUNG SKIN-ADULT: 1.4 3 E +0 2 2.315+ 02 2.T 4E +02 4. 69 5+ 02 .8 19E+02 L&. s2 E+ 04 0.00E+00 0.30i+00 TE5N: 1. 9 7 E + 0 2 3. 27 2+ 0 2 3. 8 5 E + 02 6 49 E+ 0 2 1.14 E +0 3 ' 9.2 6 5+ 04 0.00E+00.0.00E+00 CHILO: 2.44E+02 1.745+02 5.25E+02 6 44E+02 1.07E+03 1.22i+05 0.00E+00 0.00E+00~ INFANT: 1. 7 3 E + 0 2 6. 33 d + U 1 4. 2 0 E + 0 2 5. 0 d E+ 0 2 7.10 E+ 0 2 1.13 3 + 05 ' 0. 0 0 E + 0 0 0.00E+00 u I g..:.. 4.. . . a
>-,e --e- ,E~ -we- w --e- , , - _ - - - - - ,. , . . - - - E-.,e---. . .--..,-# --- .%.. , - - - - - . e-. --
. . _ ,. .. . . . .. . . . .: :. . . ~ _ _ _ _ -.-.:__......_...-.u._.,
.1.- ,
-1 TABLE 2-3 j
- ASSUMPTIONS USED IN LIMERICK GASEOUS EFFLUENT DOSE EVALUATION v
~
. . j
_. Index l Description 1 Value 'I i 1 Fraction of- 0.76
~2- Fraction of - -produce leafy veg from from local. garden local garden . . !
3 1.00-4- Soil density in plow -layer :(kg/m"2)i 240 GJ Fraction of deposited particulates retained on vegetation O.'20 5 Fraction of: deposited iodines retained,on
. vegetation . -
1.0: n 6- Shielding factor of residential structures 1 7 0. 7. ' 8 Period of buildup of. activity in soil (hr) 175200.0 . , Per'iod of pasture grass exposure to ,
- activity '(hr) 720.0 y '
.9 10
. Period of crop exposure to activity (hr). , 1440.0
' Transport time milkman (hr) 48.0 11
- Delay time for ingsstion of grass by' animals' (hr) 0.0 12 Delay time for ingestion of stored feed by animals-(br 2160.0 !
13 Delay time- for) ingestion of leaf veg by - 14 man (hr) 24.0 t Delay time for ingestion of other veg by man (hr) .
- 1440.0'.
15 Time between slau meat animal (br) ghter and consumption ~ of 16 480.0 17 Grass yield, wet wt (kg/s*2) '0.7 18-Other vegetation yield, wet wt (kg/m "2) 2.0 Weathering rate constant fer activity on vegetation (1./hr) ' O.0021 19' 20 Milk cow feed consumption rate (kg/ day wet) 50.0 1 21 Beef cattle feed consumption rate-(kg/ day wet) 50.0-22 Goat feed consumption rate (kg/ day wet) 6.0 23 Plume exposure adult (hr/yr) 8760.0 Plume exposure teen (hr/yr) 8760.0 ' 24 Plume exposure child (hr/yr) 8760.0 25 Plume exposure tofant (hr/yr) 26 8760;0 Ground exposure adult (hr/yr) 8760.0-
- 27 Ground exposure teen (hr/yr) 8760;0 28 Ground exposure child (hr/yr) 29 8760.0 Ground expsours infant (hr/yr) 8760.0 a.
O
*l
~ .. ..
3 . ,- ,
- i. .
.. . F. . - -
J ,
. i TABLE 2 3 (cont.)
- Index Description > Value 36- Inhalation rate adult e"3/y ) '
8000.0 ; 31 -Inhalation rate teen ( "3/yr 8000.0- ' i t' Inhalation rate child (m"3/yr) 3700.0 ! L Inhalation rate infant- (a"3/y 1400.0 , 34 Leafy veg consumption rate adu (kg/yr)' 64.0 : l'
. 35 Leafy veg consumption rate teen (kg/yr) 42.0-
~36 Leafy veg consumption- rate child ( -
26.0 , 37 Leafy veg consumption rate infant ) . 0.0; 38 Non-leafy veg consumption rate adult (kg/yr). . 520.0._ . 39- Non-leafy veg consumption rate teen (kg/yr) 630.0
- 40 Non leafy veg consumption rate child (kg/yr)- 520.0 i 41 Non leafy veg consumption rate infant y (kg/yr) 0.0 ;
- 42. Root veg consumption rate adult '(kg/yr) 0.0 43 0.0 ;
,Root Root veg consumptionrate ratechlid teen ( g/yr
/yr))
44 veg consumption 0.0 45 . Root veg consumption rate' infant (kg/yr) 0.0
' 46 Cow milk consumption rate adult (1/yr) 310.0 47 .400.0-
- 48 Cow milkconsumption Cow milk consumptionrate rate teen child - ( yr))-
yr ' 330.0 49 Cow milk consumption rate infant /yr' 330.0
. 50 Goat milk consumption rate adult /y 310.0 ,
51 Goat milk consumption rate . teen /yr 400.0 52 Goat milk consumption-rate chid- r '330.0-
~ 53 Goat milk consumption rate infant /yr) 230.0- y
- 54 Heat consumption rate adult'(kg/y ) 110.01 ;
55- Heat consumptica rate teen- /yr 65.0 56 Meat consumption rate child g/yr) 41.0 , 57 Meat consumption rate infant (kg/yr) 0.0 3 0.75 58 Fraction of year animals on pasture 59 Fractten of feed from pasture when-on pasture
- C'.88 ;
60 Fraction of year leafy veg grown 0.42-61 Atmosphere hydrogen concentration (ga/m"3) 8.0 l I 3 D
~
.. v .,
i.-- % .
. TABLE 2-4 NEAREST GASEOUS EFFLUERT DOSE RECEPTOP DISTANCES (METERS) c Plume Ground
- Inhalation
- Vegetation Heat- Cow. -Goat '
Direction Pathways . Pathway Pathway Pathway Pathway' l i N 805 2414 -3414 4 7562 0 NNE- 805 -1609 1585' O. OL NE 965- 1097 J
' 3218 4183 0 ENE 965 2414: ~3871' O 0 E- .965- 1770 1890' 6758 0 ESE 965 805
-4511- 1770- 1770 Sc '1609 3862 SS,t '
7241 7241- 0- F 1609 1609 7224 0 0 i S- 1287 1931 3018 3701 3654 l
.SSW 1609 1931 1433 -2896 .0 SW .965 1287 2835 4827 0 WSW 1287 . 1287 2134 2255 0 W 965 2574-WNW
. 4084 ' 0 0. .
- s.
- 1126 1440 0 0 0 NW- 1126 2574 6660 0 O NNW- 1448' =1931 6325 0- 0
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-APPENDIX A ,
. -j
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y _ m; e S ' TABLE AA l-I: ' L - TECHNICAL SPECIFICATION /ODC;4 MATRIX ; 1 ODCM ODCM: ' !
'l echnical Section I Equation
- 4. Specification- Requirement- Section-II L,
6.8.4.d.1. . 3.2.1 1-1 1-2 ' 1 '3 . - 1-4 i 6.8.4.d.1- 3.3.1 , 2-1 (or 2-9) 2-2 (or 2-9)= . 2-4 (or 2-10) -' 2-5 (or.2-10) 1 6.8.4.d.2,d.3 - 3.2.2 1-1
. 1-2 1-3 1 1-4 6.8.4.d.4 3.2.3 1-5
.1-6 1-7 t
!. 6.8.4.'d.5,d.6 3.2.4 1-8 1-9 - 6.8.4.d.7 3.3.2- 2-22
, 2-23 6.8.4.d.7 - 3.3.2 2-26 2-27 2-28 s 6.8.4.d.8 - 3.3.3 2-24
.- 2-25 6.8.4.d.9 - 3.3.4 2 '2-27 2-28 6.8.4.d 9 3.3.5 2 3.11.2.7 .
2 2-5 e
= w e- -- a w s-,m.- .- - - - - - - - - . ~ - - < - - . . - - , - - - - - .
i
.i
- .. . e. n TABLE'A-1 (cant.)' ODCM- ODCM Technical Section:I -Equation-Specification Requirement Section'II e 6.8.4.d.10 3.3.8 1--5 1-6 1 . 2-24 2-25 2 '2 6 - , 2-27 2-28~ 6.8.4.d.10' '3.3.7 3-1
'6.8.'4.e.1- 3.4.1 Section 4-App. B 6.8.4.e.3 3.5 'l-5
- 3 . 4 .' 3 1-6 '
1-7 2-29 2-30. , 2-31 2-32 g 3-2 l ( . l a
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l' ' APPENDIX B t RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM - . SAMPLETYPE,l LOCATION,ANDANALYSIS. i l~ 4. l I t e I s em e b 4 5 ,
-. . .. , .. - . . . - - . . _ _ . _ _ _ . , _ _ . __ _ _.,_:__,_ _ t
~
1 .
. Page 1;of.4 TABLE 8-1 -
ODCN - LIMERICK GENERATING STATION I
~
RADIOLOGICAL ENVIROMENTAL MONITORING PROGRAM ~ P k i Pathway $thtson Code Location Collection Method' Analyses
- l. Direct 3652 0.6 miles N of. site I set of four (4) TLDs Gasma dose ~il '!
- 2El 5.1 miles NNE of-site" from each location at quarterly _ !
351 0.6 miles NME of site least quarterly ;
- 4El. 4.6 miles ME of site !
SSI 0.4 miles NE-of sitel l 5HI C '25.8 miles NE of site ; I- 6C1 2.1 miles _ENE of site ! l 751 0.5 miles ENE of site l 7El 4.2 miles ENE of site - l 901. 2.2' miles E'of site 1 1053 0.5 miles' E of site- ~ i,
. .10El :- 3.9 miles E of.. site 10F3 5.5 miles ESE of site 1151 0.5 miles ESE of,. site
- _ _ 1301 2.9 biles SE of' site-i -- -
13El 4.3 miles-SE'ofusite -- '
'1451 0.6 miles SEiof-site
-1501 ~ 3.2 miles SE of site - ,
1652 0.6 miles SSE of' site .j 1781 1.6 miles.S of site.
~
g
- 12.9 miles Siof-site 118G1 -C -
t 1851 ~0.3 miles'S of' site , L 11901 3.6 miles S of site
- i 2001' '3.1 miles:SSW of site .
( 20F1 5.2 miles 'SSW of site R l 2151 0.5 alles SSW of' site - L 0.5 miles WSW of.. site-
. 23S2 s a C - Control ~ Stations-- ' ENGR -52/8 HP. ;G<&
DALE- ,oh7M REV ' 2 '
-+ ~ c- .
- . -. z. . - - . . . - _ _ _ _ = _ _ _ - - _ = _ _
- Page 2 of 4 5
1ABLE B-1 (continued)
- 6
- - -._ a o
f~ Pathway station Code location Collection Method Analyses l' Direct I. 2401' 3.9 miles-SW of site Collected quarterly-. Ganssa dose l (cont.) 2551 0.5 alles SW of site . quarterly i 25D1 4.0 miles WSW of site
. -2653 0.4 alles W of site j '2802 3.8 miles W of site .
29S1 0.5 miles lefW of site . 2901 4.9 miles WW of site i 3101 3.R miles NW of site : i 3102 3.9 alles NW of site 32SI 0.6 miles NW of site 3452 0.6 alles Mini of site f 34El 4.6 miles NNW ef' site
; 35ft 4.2 elles N of site I ~
f II. Airborne i Particulates 1953 0.5 miles E of site Approximately I cfm Gross beta analysis { 1151 0.5 miles ESE -i site continuous flow through
- on each weekly l
1451 0,6 jolles $E of site glas's fiber fliter which -sample. Gaassa. spec-1301 2.9 miles SE of site .$s collected weekly at trometry shall be done
-l 13H4 C 28.8 alles SE of site - :f81ter change. ~when gross beta exceeds
' .. ,-ten ttees'the yearly
' man of control station value.
l - l' ENGR G 4/2 lfp jer6
^
i j DATE F4/# '
; REV p .
~
r..._.m - - - - - - - - - - - ' "
- m. m . ...,_ .*,.-_m . . - - . . - - - - - - - - - - - - - - - - - - . _ - ---
q TABLE.B-1 (continued) ~l r . Pathway Station Code -Location Collection Hethod Analyses i
- 11. Airborne-(cont.) -:
Particulates (cont.) ~ Gross beta analysis done >24 hr after samp1tng to allow for Radon and Thoron
-daughter decay. --
Gamma isotopic analysis-' l on acnthly compostte. Iodine 1053- 0.5 miles E of site . - A TEDA impregnated Iodine 131 analysis 1151 0.5 alles ESE of site flow-through cartridge performed on each' 1451 0.6 miles SE of site is: connected to air . weekly sample.- 13C1 -2.9 miles SE of site sampler and Is collected ',
- -13H4 -C 28.8 miles SE of site ,
weekly at filter change.- III. FA E - Surface .2451 ~C ~ 0.3 Wiles SSW of site - ~ Sample collected from a Gamma Isotopic a 1682- 1.1 elles SSE of site- continuous' water sampler, : analysis monthly;.
- monthly. In event sampler H-3 on quarterly is Inoperable, weekly-grab composite.
samples ~will.be collected untti sampler returned to -
~ service. .
Sediment 16C4- : Vincent Dam, Down- A sediment. sample Is taken' '. Gamma'Isetopic'
-stream of discharge semi-annually. . analysis; semi-annually.
Ek NE
~ '
4
- IIP . Ja<5 .
DATE J/,N S - _ REV - -7 '
" ~' *---. - - __- - _ - -- - _ _ - - _ _ _ _ _ _ _ _ _ _ _ _ . _ _ ___ -
- ' " * - -Ve _ _ _ -4 4 __-- __-__:a_--__.--_ _s.-_-_..__ -_-____..__,__.c_-____---.2 -
u______ ______ _ _ - _ _ _ _ _ _ _ _ - _ _ _ _ _ - _ ____ _ s
' Tabu B-1 (continued) Page 4 cf 4 ~
Pathway Station Code location ~ Collection Method' Analyses-IV. Incestion
- L Hlik 22F1 C 9.8 miles SW of site 1981 Sample of fresh'alik is Gasma isotopic and-1.1 miles ESE of site 'I 2581 1.3 miles WSW of site collected from each farm I-131 analyses on j biweekly when cows are'on 2181 1.8 miles SSW of site .each sample'on-pasture, monthly at other. collection.
1
. times ' .;
4 Drinking 15f7 5.2 miles SSE of site Sample collected from a 28F3 C ~ 5.9 miles l#fW of site Gross beta and
'15f4 continuous water sampler gamma isotopic 7.8 alles SE of site monthly. .In event sampler 1602 2.4 elles SSE of site monthly; H-3 on is inoperable, weekly grab quarterly composite samples will be' collected ';'
untti sampler returned to service Fish 1605 1.9 alles SSE of site 2901 Two sper.les of recrea- Gamma isotopic C 3.2 elles l#1W of- site tionally important-fish- I- , analyses on- '*' ! (predator and bottom edible. portions
- i feeder) sampled In~ season ,
l or semiannually If not seasonal .. ( food 1151 0.5 miles ESE of site : Products Monthly When available Gamma isotopic. if milk.samp1tng is not and I-131 analysis t performed-i EsGR N3s - MP _ F.CG ' DATE _ ,@ i N REV 9, i 1 . .
eemose 4 een e. . W3. e .L. .. p. J,+ . p ,, p i . . s ,, .. . ,,g .,. ..g....s.;3,es,,,......-.,_..
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