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{{#Wiki_filter:ACCELERATEDDISTSJBUTIONDEMONSTFWTIONSYSTEMREGULATORINFORMATIONDZSTRIBUTZONeSTEM(RIDE)/~,ACCESSIONNBR:9009110036DOC.DATE:90/08/30NOTARIZED:NODOCKETFACIL:50-220NineMilePointNuclearStation,Unit1,NiagaraPowe0500220AUTH.NAMEAUTHORAFFILIATIONFIRLITFJ.F.NiagaraMohawkPowerCorp.RECIP.NAMERECIPIENTAFFILIATIONDocumentControlBranch(DocumentControlDesk)
{{#Wiki_filter:ACCELERATED DISTSJBUTION DEMONSTFWTION SYSTEMREGULATOR INFORMATION DZSTRIBUTZONeSTEM (RIDE)/~,ACCESSION NBR:9009110036 DOC.DATE:
90/08/30NOTARIZED:
NODOCKETFACIL:50-220 NineMilePointNuclearStation,Unit1,NiagaraPowe0500220AUTH.NAMEAUTHORAFFILIATION FIRLITFJ.F.
NiagaraMohawkPowerCorp.RECIP.NAME RECIPIENT AFFILIATION DocumentControlBranch(Document ControlDesk)


==SUBJECT:==
==SUBJECT:==
Forwards"SemiannualRadioactiveEffluentReleaseReptforJan-June1990"&Rev6-8ofODCM.IDISTRIBUTIONCODE:ZE48DCOPIESRECEIVED:LTR)ENCLgSIZE:4'fTITLE:50.36a(a)(2)SemiannualEffluentReleaseReportsNOTES:RECIPIENTIDCODE/NAMEPD1-1LAMARTIN,R.INTERNAL:ACRSTECHADVRE~01RGN1DRSS/RPBEXTERNAL:BNLTICHLER,J03NRCPDRCOPIESLTTRENCL1111221111RECIPIENTIDCODE/NAMEPD1-1PDAEOD/DSP/TPABNRR/DREP/PRPB11RESBROOKS,BRGN1FILE02EG&GSIMPSON,FCOPIESLTTRENCL111122111122DDDNOTETOALL"RIDS"RECIPIENTS:PLEASEHELPUSTOREDUCEWAS'ONTACTTHEDOCUMENTCONTROLDESK,ROOMPl-37(EXT.20079)TOELIMINATEYOURNAMEFROMDISTRIBUTIONLINISFORDOCUMENTSYOUDON'TNEED!DDTOTALNUMBEROFCOPIESREQUIRED:LTTR19ENCL  
Forwards"Semiannual Radioactive EffluentReleaseReptforJan-June1990"&Rev6-8ofODCM.IDISTRIBUTION CODE:ZE48DCOPIESRECEIVED:LTR
'v"gg~swr~0LIrf*(4) i4NINEMILEPOINTNUCLEARSTATION/P.O.BOX32,LYCOMING,N.Y.13093/TELEPHONE(315)343-2110August30,1990U.S.NuclearRegulatoryCommissionAttn:DocumentControlDeskWashington,DC20555RE:NineMilePointUnitg1DocketNo.50-220DPR-63Gentlemen:InconformancewiththeNineMilePointNuclearStationUnitglTechni~calSpecifications,weareenclosingtheSemi-AnnualRadioactiveEffluentReleaseReortfortheperiodJanuary1,1990,throughJune30,1990.Includedinthisreportisasummaryofliquid,gaseousandsolideffluentsreleasedfromthestationduringthereportingperiod(Tables1-3),adescriptionofandjustificationforrecentrevisionstotheOffsiteDoseCalculationManual(ODCM)(Table4),anexplanationastothecauseandcorrectiveactionsregardingtheinoperabilityofanyStationLiquidand/orGaseousEffluentMonitoringinstrumentation(Table5,andAttachment1),adescriptionofrecentrevisionstotheProcessControlProgram(PCP)(Table6),andanupdateofactualdataforthemonthofDecemberusedinthefourthquarteroftheJuly-December1989Semi-AnnualRadioactiveEffluentReleaseReport(Table7).Copiesofrevision6,7and8oftheUnit1ODCMandrequiredtechnicalreviewdocumentationarealsoenclosed.ITheformatusedfortheeffluentdataisoutlinedinAppendixBofRegulatoryGuide1.21,Revision1.Doseassessmentsweremadein,accordancewiththeNMP-1Off-SiteDoseCalculationManual.DistributionisinaccordancewithRegulatoryGuide'0.1,10CFR50.4(b)(1)andtheTechnicalSpecifications.Ifyouhaveanyquestionsconcerningtheattachedreport,pleasecontactGaryCorell,ChemistryUnitSupervisor,atNineMilePointUnit1(315)349-2070.Verytrulyyours,900911003b900830PDRADQCN,05000220RPNUJFF/lmcEnclosures(3copies)osephFFirlitVicePresident-NuclearGeneration I~r t,Page2U.S.NuclearRegulatoryCommissionAugust30,1990xc:Director,OfficeofNuclearReactorRegulation(1)Director,OfficeofInspectionandEnforcement(1)Mr.ThomasT.Martin,RegionalAdministrator,UnitedStatesNuclearRegulatoryCommission,RegionI,AllendaleRd.,KingofPrussia,Pennsylvania19406(1)NRCResidentInspector,NineMilePointNuclearStationUnit51(1)NewYorkStateEnergyOffice,2RockefellerPlaza,Albany,NY12223Attn:Ms.DonnaRoss OFF-SITEDOSECALCULATIONMANUALNINEMILEPOINTUNIT.1  
)ENCLgSIZE:4'fTITLE:50.36a(a)(2)
Semiannual EffluentReleaseReportsNOTES:RECIPIENT IDCODE/NAME PD1-1LAMARTIN,R.
INTERNAL:
ACRSTECHADVRE~01RGN1DRSS/RPBEXTERNAL:
BNLTICHLER,J03 NRCPDRCOPIESLTTRENCL1111221111RECIPIENT IDCODE/NAME PD1-1PDAEOD/DSP/TPAB NRR/DREP/PRPB11 RESBROOKS,BRGN1FILE02EG&GSIMPSON,F COPIESLTTRENCL111122111122DDDNOTETOALL"RIDS"RECIPIENTS:
PLEASEHELPUSTOREDUCEWAS'ONTACT THEDOCUMENTCONTROLDESK,ROOMPl-37(EXT.20079)TOELIMINATE YOURNAMEFROMDISTRIBUTION LINISFORDOCUMENTS YOUDON'TNEED!DDTOTALNUMBEROFCOPIESREQUIRED:
LTTR19ENCL  
'v"gg~swr~0LIrf*(4) i4NINEMILEPOINTNUCLEARSTATION/P.O.
BOX32,LYCOMING, N.Y.13093/TELEPHONE (315)343-2110August30,1990U.S.NuclearRegulatory Commission Attn:DocumentControlDeskWashington, DC20555RE:NineMilePointUnitg1DocketNo.50-220DPR-63Gentlemen:
Inconformance withtheNineMilePointNuclearStationUnitglTechni~cal Specifications, weareenclosing theSemi-Annual Radioactive EffluentReleaseReortfortheperiodJanuary1,1990,throughJune30,1990.Includedinthisreportisasummaryofliquid,gaseousandsolideffluents releasedfromthestationduringthereporting period(Tables1-3),adescription ofandjustification forrecentrevisions totheOffsiteDoseCalculation Manual(ODCM)(Table4),anexplanation astothecauseandcorrective actionsregarding theinoperability ofanyStationLiquidand/orGaseousEffluentMonitoring instrumentation (Table5,andAttachment 1),adescription ofrecentrevisions totheProcessControlProgram(PCP)(Table6),andanupdateofactualdataforthemonthofDecemberusedinthefourthquarteroftheJuly-December1989Semi-Annual Radioactive EffluentReleaseReport(Table7).Copiesofrevision6,7and8oftheUnit1ODCMandrequiredtechnical reviewdocumentation arealsoenclosed.
ITheformatusedfortheeffluentdataisoutlinedinAppendixBofRegulatory Guide1.21,Revision1.Doseassessments weremadein,accordance withtheNMP-1Off-SiteDoseCalculation Manual.Distribution isinaccordance withRegulatory Guide'0.1, 10CFR50.4 (b)(1)andtheTechnical Specifications.
Ifyouhaveanyquestions concerning theattachedreport,pleasecontactGaryCorell,Chemistry UnitSupervisor, atNineMilePointUnit1(315)349-2070.
Verytrulyyours,900911003b 900830PDRADQCN,05000220RPNUJFF/lmcEnclosures (3copies)osephFFirlitVicePresident
-NuclearGeneration I~r t,Page2U.S.NuclearRegulatory Commission August30,1990xc:Director, OfficeofNuclearReactorRegulation (1)Director, OfficeofInspection andEnforcement (1)Mr.ThomasT.Martin,RegionalAdministrator, UnitedStatesNuclearRegulatory Commission, RegionI,Allendale Rd.,KingofPrussia,Pennsylvania 19406(1)NRCResidentInspector, NineMilePointNuclearStationUnit51(1)NewYorkStateEnergyOffice,2Rockefeller Plaza,Albany,NY12223Attn:Ms.DonnaRoss OFF-SITEDOSECALCULATION MANUALNINEMILEPOINTUNIT.1  
:~vr"<<.J'qw(,W~Pg ODCH-NINEMILEPOINTUNIT1TABLEOFCONTENTS
:~vr"<<.J'qw(,W~Pg ODCH-NINEMILEPOINTUNIT1TABLEOFCONTENTS


==1.0INTRODUCTION==
==1.0INTRODUCTION==
2.0LIQUIDEFFLUENTS2.1SetpointDeterminations2.1.1Basis2.1.2ServiceWaterSystemEffluentAlarmSetpoint2.1.3LiquidRadwasteEffluentAlarmSetpoint2.1.4Discussion2.1.4.1ControlofLiquidEffluentBatchDischarges'::2:1-'."4:2'>.Simultaneous:Discharges.of'RadioactiveLiquids2.1.4.3SampleRepresentativeness2.1.4.4LiquidRadwasteSystemOperation2.1.4.5ServiceWaterSystemContamination'.2-'iquidEffluentConcentrationCalculation~Pae~-102.32.3.13.03.13.1.13.1.23.1.3DoseDeterminationsMaximumDoseEquivalentPathwayGASEOUSEFFLUENTS'SetpointDeterminationsBasisStackMonitorSetpointsRecombiner.Discharge(OffGas)MonitorSetpoints121217171718213.1.4EmergencyCondenserVentMonitorSetpoint223.1.53.1.5.13.1.5.2DiscussionStackEffluentMonitoringSystemDescriptionStack.SampleFlowPath-RAGEHS2323.3.1.5.3.StackSampleFlowPath-OGESHS25 Ae,f/''f,iI4)"4'pa'tkW ODCM-NINEMILEPOINTUNIT1TABLEOFCONTENTS(Cont'd)3.1.5.4-SampleFrequency/SampleAnalysis=3.1.5.5I-133Estimates3,1.5.6GaseousRadwasteTreatmentSystemOperation~Pae2627273.23.2.1DoseandDoseRateDeterminationDoseRate28313.2.1.1NobleGases3.2.1.2Tritium,IodinesandParticulates31333.2.2Dose353.2.2.1NobleGasAirDose3.2.2.2TritiumIodinesandParticulates3.2.2.3AccumulatingDoses3637383.3CriticalReceptors39e4.O4.140CFR190REQUIREMENTSEvaluationofDosesFromLiquidEffluents3.4RefinementofOffsiteDosesResultingFromEmergencyCondenserVentReleases41424.2'.34.45.05.15.25.3EvaluationofDosesFromGaseousEffluentsiEvaluation"ofDosesFromDirectRadiationDosestoMembersofthePublicNithintheSiteBoundaryENVIRONMENTALMONITORINGPROGRAMSamplingStationsInterlaboratoryComparisonProgramCapabilitiesforThermoluminescentDosimetersUsedforEnvironmentalMeasurements.484849535556  
 
<<YIU'',L'b4QtgI ODCH-NINEMILEPOINTUNIT1TABLEOFCONTENTS(Cont'd)~PaeTablel-lAverageEnergyPerDisintegrationTables2-1AiatValuesfortheNMP-1Facilityto2-8Table3-1CriticalReceptor-DispersionParametersforGround.LevelandElevatedReleasesTable3-2GammaAirandHholeBodyPlumeShineDoseFactorsforNobleGases(BiandVi)Table3-3ImmersionDoseFactorsforNobleGasesTables3-4'''to3-22">>OrganDoseandDoseRateFactors(Ri)Table5-1NMP-1RadiologicalEnvironmentalMonitoringProgramSamplingLocationsFigure5.1-1NineMile'ointOn-S/teHapFigure5.1-2.NineMilePointOffsiteHap5960.68697071909495AppendixALiquidDoseFactorDerivation(Aiat)AppendixBPlumeShineDoseFactorDerivation(BiandVi)...AppendixC.OrganDoseandDoseRateFactorsforIodine-131and133,ParticulatesandTritiumDerivation(Ri)AppendixDDiagramsofLiquidandGaseousRadwasteTreatmentSystems97100104115 l>dI1a  
==2.0 LIQUIDEFFLUENTS==
2.1SetpointDeterminations 2.1.1Basis2.1.2ServiceWaterSystemEffluentAlarmSetpoint2.1.3LiquidRadwasteEffluentAlarmSetpoint2.1.4Discussion 2.1.4.1ControlofLiquidEffluentBatchDischarges
'::2:1-'."4:2'>.Simultaneous:
Discharges.of'Radioactive Liquids2.1.4.3SampleRepresentativeness 2.1.4.4LiquidRadwasteSystemOperation 2.1.4.5ServiceWaterSystemContamination
'.2-'iquidEffluentConcentration Calculation
~Pae~-102.32.3.13.03.13.1.13.1.23.1.3DoseDeterminations MaximumDoseEquivalent PathwayGASEOUSEFFLUENTS
'Setpoint Determinations BasisStackMonitorSetpoints Recombiner.
Discharge (OffGas)MonitorSetpoints 121217171718213.1.4Emergency Condenser VentMonitorSetpoint223.1.53.1.5.13.1.5.2Discussion StackEffluentMonitoring SystemDescription Stack.SampleFlowPath-RAGEHS2323.3.1.5.3.StackSampleFlowPath-OGESHS25 Ae,f/''f,iI4)"4'pa'tkW ODCM-NINEMILEPOINTUNIT1TABLEOFCONTENTS(Cont'd)3.1.5.4-SampleFrequency/Sample Analysis=
3.1.5.5I-133Estimates 3,1.5.6GaseousRadwasteTreatment SystemOperation
~Pae2627273.23.2.1DoseandDoseRateDetermination DoseRate28313.2.1.1NobleGases3.2.1.2Tritium,IodinesandParticulates 31333.2.2Dose353.2.2.1NobleGasAirDose3.2.2.2TritiumIodinesandParticulates 3.2.2.3Accumulating Doses3637383.3CriticalReceptors 39e4.O4.140CFR190REQUIREMENTS Evaluation ofDosesFromLiquidEffluents 3.4Refinement ofOffsiteDosesResulting FromEmergency Condenser VentReleases41424.2'.34.45.05.15.25.3Evaluation ofDosesFromGaseousEffluents iEvaluation" ofDosesFromDirectRadiation DosestoMembersofthePublicNithintheSiteBoundaryENVIRONMENTAL MONITORING PROGRAMSamplingStationsInterlaboratory Comparison ProgramCapabilities forThermoluminescent Dosimeters UsedforEnvironmental Measurements.
484849535556  
<<YIU'',L'b4QtgI ODCH-NINEMILEPOINTUNIT1TABLEOFCONTENTS(Cont'd)~PaeTablel-lAverageEnergyPerDisintegration Tables2-1AiatValuesfortheNMP-1Facilityto2-8Table3-1CriticalReceptor-Dispersion Parameters forGround.LevelandElevatedReleasesTable3-2GammaAirandHholeBodyPlumeShineDoseFactorsforNobleGases(BiandVi)Table3-3Immersion DoseFactorsforNobleGasesTables3-4'''to3-22">>OrganDoseandDoseRateFactors(Ri)Table5-1NMP-1Radiological Environmental Monitoring ProgramSamplingLocations Figure5.1-1NineMile'oint On-S/teHapFigure5.1-2.NineMilePointOffsiteHap5960.68697071909495AppendixALiquidDoseFactorDerivation (Aiat)AppendixBPlumeShineDoseFactorDerivation (BiandVi)...Appendix C.OrganDoseandDoseRateFactorsforIodine-131and133,Particulates andTritiumDerivation (Ri)AppendixDDiagramsofLiquidandGaseousRadwasteTreatment Systems97100104115 l>dI1a  


==1.0INTRODUCTION==
==1.0INTRODUCTION==
'heOffsiteDoseCalculationManual(ODCM)providesthemethodologytobeusedfordemonstratingcompliancewiththeRadiologicalEffluentTechnicalSpecifications(RETS),10CFR20,10CFR50,and40CFR190.ThecontentsoftheODCMarebased-on.,DraftNUREG-0472,Revision3,"StandardRadiological'EffluentTechnical;SpecificationsforPressurizedHater...Reactors,"'September1982;DraftNUREG-0473,Revision2."RadiologicalEffluentTechnicalSpecificationsforBNR's","July1979;NUREG0133,"PreparationofRadiologicalEffluentTechnicalSpecificationsforNuclearPowerPlants,"October1978;theseveralRegulatoryGuidesreferencedinthesedocuments;and,communicationwiththeNRCstaff.Section5containsadetaileddescriptionoftheRadiological.EnvironmentalMonitoring,(REM)samplinglocations.ShoulditbenecessarytorevisetheODCM,theserevisionswi11bemadeinaccordancewithTechnicalSpecifications.  
 
'pItI'0IIHg 2.0LIQUIDEFFLUENTS2.1SetpointDeterminations2.1.1BasisMonitorsetpointswillbeestablishedsuchthattheconcentrationofradionuclidesintheliquideffluentreleasesinthedischargecanalwillnotexceedthoseconcentrationsas-specifiedin10CFR20,Appendix8,TableII,Column2.SetpointsfortheServiceHaterSystemEffluentLinewillbecalculatedquarterlybasedontheradionuclidesidentifiedduringthepreviousyear'sreleasesfromtheliquidradwastesystemortheisotopesidentifiedinthemostrecentradwasteIreleaseorotheridentifiedprobablesource.SetpointsfortheLiquidRadwasteEffluentLinewillbebasedontheradionuclidesidentifiedineachbatchofliquidwastepriortoitsrelease.Afterrelease,theLiquidRadwastemonitorsetpointmayremainasset,orrevertbacktoasetpointbasedonaprevious<;-Semi-Annual,RadioactiveEffluentReleaseReport,orinstallblankflangeinthedischargelineanddeclareinoperableinaccordancewiththetechnicalspecification.SincetheServiceHaterSystemeffluentmonitorandLiquidRadwasteeffluentmonitorcanonlydetectgammaradiation,the.alarmsetpointsarecalculatedbyusingtheconcentrationofgammaemittingisotopesonly(orthecorrespondingMPCvaluesforthesameisotopes,whicheverarehigher)intheX>(uC1/mi)i>expression(Section2.1.2,2.1.3).
'heOffsiteDoseCalculation Manual(ODCM)providesthemethodology tobeusedfordemonstrating compliance withtheRadiological EffluentTechnical Specifications (RETS),10CFR20,10CFR50,and40CFR190.ThecontentsoftheODCMarebased-on.,Draft NUREG-0472, Revision3,"Standard Radiological
0kj'-,lIPh'LIll4v'h(\~T~t.+fI+y4g~~~q+~fCal44 2.1.1(Cont'd)TheRequiredDilutionFactoriscalculatedusingconcentrationsofallisotopespresent(orthecorrespondingHPCvaluesfor-thesameisotopes,whicheverarehigher)includingtritiumand'othernon-gammaemitterstoensurethatallradionuclidesinthedischargecanaldonotexceed10CFR20limits~2.1.2.::-ServiceWaterSystemEffluentLineAlarmSetpointThedetailedmethodsforestablishingsetpointsfortheServiceWaterSystemEffluentLineMonitorshallbecontainedintheNineMilePointStationProcedures.Thesemethodsshallbeinaccordancewiththefollowing:~Setpoint(Hialarm)<0.9Setpoint(Alertalarm)<6.7(uC1/m1>sy<CF)lTDF/Fsw2-[(uCi/ml)iT/MPCi]il(UCi/ml)i~(CF)TOF/FswZ;[(uCi/ml)iT/HPCi]+background+background(uCi/ml)igconcentrationofgammaemittingisotopeiinthesample,orthe.."-.-'correspondingMPCof,gammaemittingisotopei(HPC)ig,whicheverishigher(unitsuCi/ml).(uCt/ml)iTconcentrationofanyradioactiveisotopeiinthesampleincludingtritiumandothernon-gammaemittersorcorrespondingMPCofisotopei,MPCi,whicheverishigher(unitsuCi/ml).'OF.'TotalOilutionFlow(unitsgallons/min)FswCFHPCiServiceWaterFlow(unitsgallons/min)monitorcalibrationfactor(unitsnetcpm/uCi/ml)liquideffluentradioactivityconcentrationslimitforradionuclideiasspecifiedin10CFR20,AppendixB,TableII,Column2.
'Effluent Technical;Specifications forPressurized Hater...Reactors,"'September 1982;DraftNUREG-0473, Revision2."Radiological EffluentTechnical Specifications forBNR's","July1979;NUREG0133,"Preparation ofRadiological EffluentTechnical Specifications forNuclearPowerPlants,"October1978;theseveralRegulatory Guidesreferenced inthesedocuments; and,communication withtheNRCstaff.Section5containsadetaileddescription oftheRadiological
.Environmental Monitoring,(REM) samplinglocations.
Shoulditbenecessary torevisetheODCM,theserevisions wi11bemadeinaccordance withTechnical Specifications.  
'pItI'0IIHg  
 
==2.0 LIQUIDEFFLUENTS==
2.1SetpointDeterminations 2.1.1BasisMonitorsetpoints willbeestablished suchthattheconcentration ofradionuclides intheliquideffluentreleasesinthedischarge canalwillnotexceedthoseconcentrations as-specified in10CFR20,Appendix8,TableII,Column2.Setpoints fortheServiceHaterSystemEffluentLinewillbecalculated quarterly basedontheradionuclides identified duringthepreviousyear'sreleasesfromtheliquidradwastesystemortheisotopesidentified inthemostrecentradwasteIreleaseorotheridentified probablesource.Setpoints fortheLiquidRadwasteEffluentLinewillbebasedontheradionuclides identified ineachbatchofliquidwastepriortoitsrelease.Afterrelease,theLiquidRadwastemonitorsetpointmayremainasset,orrevertbacktoasetpointbasedonaprevious<;-Semi-Annual, Radioactive EffluentReleaseReport,orinstallblankflangeinthedischarge lineanddeclareinoperable inaccordance withthetechnical specification.
SincetheServiceHaterSystemeffluentmonitorandLiquidRadwasteeffluentmonitorcanonlydetectgammaradiation, the.alarmsetpoints arecalculated byusingtheconcentration ofgammaemittingisotopesonly(orthecorresponding MPCvaluesforthesameisotopes, whichever arehigher)intheX>(uC1/mi)i>
expression (Section2.1.2,2.1.3).
0kj'-,lIPh'LIll4v'h(\~T~t.+fI+y4g~~~q+~fCal44 2.1.1(Cont'd)TheRequiredDilutionFactoriscalculated usingconcentrations ofallisotopespresent(orthecorresponding HPCvaluesfor-thesameisotopes, whichever arehigher)including tritiumand'othernon-gamma emitterstoensurethatallradionuclides inthedischarge canaldonotexceed10CFR20limits~2.1.2.::-Service WaterSystemEffluentLineAlarmSetpointThedetailedmethodsforestablishing setpoints fortheServiceWaterSystemEffluentLineMonitorshallbecontained intheNineMilePointStationProcedures.
Thesemethodsshallbeinaccordance withthefollowing:
~Setpoint(Hialarm)<0.9 Setpoint(Alertalarm)<6.7 (uC1/m1>sy
<CF)lTDF/Fsw2-[(uCi/ml)iT/MPCi]
il(UCi/ml)i~
(CF)TOF/FswZ;[(uCi/ml)iT/HPCi]
+background
+background (uCi/ml)ig concentration ofgammaemittingisotopeiinthesample,orthe.."-.-'corresponding MPCof,gammaemittingisotopei(HPC)ig,whichever ishigher(unitsuCi/ml).(uCt/ml)iT concentration ofanyradioactive isotopeiinthesampleincluding tritiumandothernon-gamma emittersorcorresponding MPCofisotopei,MPCi,whichever ishigher(unitsuCi/ml).'OF.'TotalOilutionFlow(unitsgallons/min)
FswCFHPCiServiceWaterFlow(unitsgallons/min) monitorcalibration factor(unitsnetcpm/uCi/ml) liquideffluentradioactivity concentrations limitforradionuclide iasspecified in10CFR20,AppendixB,TableII,Column2.
4<<~65~1q~~
4<<~65~1q~~
2.1.2(Cont'd)Sample(MPC)i0.9and0.7[(uCi/ml)iT/MPCi]TDF/FswThosenuclidespresentinthepreviousbatchreleasefromtheliquidradwasteeffluentsystemorthosenuclidespresentinthelastSemi-annualRadioactiveEffluentReleaseReport(unitsuCi/ml)orthosenuclidespresentintheservicewatersystem.**sameasMPCibutforgammaemittingnuclidesonly.factorsofconservatismtoaccountforinaccuracies.RequiredDilutionFactor.IfMPCvaluesareusedintheZ(uCi/ml)iy,theymustalsobeusedincalculatingROF(numerator).ActualDilutionFactor2.1.3LiquidRadwasteEffluentLineAlarmSetpointThe;detailedmethodsforestablishingsetpointsfortheLiquidRadwaste'ffluentLineMonitorshallbecontainedintheNineMilePointStationProcedures.Thesemethodsshallbeinaccordancewiththefollowing:Setpoint(Hi-Hialarm)<0.9(uCi/ml)ig(CF)Setpoint(Hialarm)<0.7(uCi/ml)ig(CF)TDF/Fre[(uCi/ml)iT/MPC]TDF/FreZ;[(uCi/ml)iT/HPCi]background+background(uCi/ml)iyconcentrationofgammaemittingisotopeiinthesampleor,thecorrespondingMPCofgammaemittingisotopei(HPC)i."whicheverishigher.(uCi/ml)iTconcentrationofanyradioactiveisotopeiinthesampleincludingtritiumandothernon-gammaemittersorthecorrespondingHPCofisotopeiHPCiwhicheverishigh'er.(unitsuCi/ml)TDFFreCFTotalDilutionFlow(unitsgallons/min).RadwasteEffluentFlow(unitsgallons/min)monitorcalibrationfactor(unitsnetcps/uCi/ml)**ForperiodswithknownreactorwatertoRCLCsystemleakage,RCLCmaximumpermissibleconcentrationmaybeprudentlysubstitutedfortheabove.
2.1.2(Cont'd)Sample(MPC)i0.9and0.7[(uCi/ml)iT/MPCi]
4.C(I Mpci(HPC)i.0.9and0.7liquideffluentradioactivityconcentrationlimitforradionuclideiasspecifiedin10CFR20,AppendixB,TableII,Column2,forthosenuclidesdetectedbyspectralanalysisofthecontentsoftheradwastetankstobereleased.(unitsuCi/ml)sameasHPCibutforgammaemittingnuclideonly.factorsofconservatismtoaccountforinaccuracies.X;[(uCi/ml)iT/HPCi]RequiredDilutionFactor.IfHPCvaluesareusedintheX(uCi/ml)ix',theymustalsobeusedincalculatingRDF(numerator).Notes:(a)IfTDF/Fregf(uCi/ml)iT/MPCi]thedischargecouldnotbemade,sincethemonitorwouldbecontinuouslyinalarm.Toavoidthissituation,Fwillbereduced(normallybyafactorof2)toallowsettingthealarmpointataconcentrationhigherthantankconcentration.Thi's.wil.lalso'resultinadischargecanalconcentrationatapproximately50Kmaximumpermissibleconcentration.(b)ThevalueusedforTDFwillbereducedbythefractionalquantity(1-FT),.whereFTis,temperingfraction(i.e.,diversionofsomefractionofdischargeflowtotheintakecanalforthepurposeoftemperaturecontrol).
TDF/FswThosenuclidespresentinthepreviousbatchreleasefromtheliquidradwasteeffluentsystemorthosenuclidespresentinthelastSemi-annual Radioactive EffluentReleaseReport(unitsuCi/ml)orthosenuclidespresentintheservicewatersystem.**
8+4%II'trf~x.C' 2.1.4Discussion2.1.4.1ControlofLiquidEffluentBatchDischargesAtNineMilePointUnit1LiquidRadwasteEffluentsarereleasedonly'nabatchmode.Topreventtheinadvertentreleaseofanyliquidradwasteeffluents,radwastedischargeismechanicallyisolated(blankflangeinstalledordischargevalvechain-lockedclosed)followingthecompletionofabatchreleaseorseriesofbatchreleases.,ThismechanicalisolationremainsinplaceandwillonlyberemovedpriortothenextseriesofliquidradwastedischargesafterallanalysesrequiredinstationproceduresandTechnicalSpecificationTable4.6.15-1Aareperformedandmonitorsetpointshavebeenproperlyad]usted.2.1.4.2SimultaneousDischargesofRadioactiveLiquids..'<<"If.duringthedischargeofanyliquidradwastebatch,thereisanindicationthattheservicewatercanalhasbecomecontaminated(throughaservicewatermonitoralarmorthroughagrabsampleanalysisintheeventthattheservicewatermonitorisinoperable)thedischargeshallbe.terminatedimmediately.Theliquidradwastedischargeshallnotbecontinueduntilthecauseoftheservicewateralarm(orhighgrabsampleanalysisresult)hasbeendeterminedandtheappropriatecorrectivemeasurestakentoensure10CFR20,Appendix8,TableII,Column2(TechnicalSpecificationSection3.6.15.a(1))limitsarenotexceeded.
sameasMPCibutforgammaemittingnuclidesonly.factorsofconservatism toaccountforinaccuracies.
RequiredDilutionFactor.IfMPCvaluesareusedintheZ(uCi/ml)i y,theymustalsobeusedincalculating ROF(numerator).
ActualDilutionFactor2.1.3LiquidRadwasteEffluentLineAlarmSetpointThe;detailed methodsforestablishing setpoints fortheLiquidRadwaste'ffluentLineMonitorshallbecontained intheNineMilePointStationProcedures.
Thesemethodsshallbeinaccordance withthefollowing:
Setpoint(Hi-Hialarm)<0.9(uCi/ml)ig (CF)Setpoint(Hialarm)<0.7(uCi/ml)ig (CF)TDF/Fre[(uCi/ml)iT/MPC
]TDF/FreZ;[(uCi/ml)iT/HPCi]
background
+background (uCi/ml)i yconcentration ofgammaemittingisotopeiinthesampleor,thecorresponding MPCofgammaemittingisotopei(HPC)i."whichever ishigher.(uCi/ml)iT concentration ofanyradioactive isotopeiinthesampleincluding tritiumandothernon-gamma emittersorthecorresponding HPCofisotopeiHPCiwhichever ishigh'er.(unitsuCi/ml)TDFFreCFTotalDilutionFlow(unitsgallons/min)
.Radwaste EffluentFlow(unitsgallons/min) monitorcalibration factor(unitsnetcps/uCi/ml)
**ForperiodswithknownreactorwatertoRCLCsystemleakage,RCLCmaximumpermissible concentration maybeprudently substituted fortheabove.
4.C(I Mpci(HPC)i.0.9and0.7liquideffluentradioactivity concentration limitforradionuclide iasspecified in10CFR20,AppendixB,TableII,Column2,forthosenuclidesdetectedbyspectralanalysisofthecontentsoftheradwastetankstobereleased.
(unitsuCi/ml)sameasHPCibutforgammaemittingnuclideonly.factorsofconservatism toaccountforinaccuracies.
X;[(uCi/ml)iT/HPCi]
RequiredDilutionFactor.IfHPCvaluesareusedintheX(uCi/ml)ix',
theymustalsobeusedincalculating RDF(numerator).
Notes:(a)
IfTDF/Fregf(uCi/ml)iT/MPCi]
thedischarge couldnotbemade,sincethemonitorwouldbecontinuously inalarm.Toavoidthissituation, Fwillbereduced(normally byafactorof2)toallowsettingthealarmpointataconcentration higherthantankconcentration.
Thi's.wil.lalso'resultinadischarge canalconcentration atapproximately 50Kmaximumpermissible concentration.
(b)ThevalueusedforTDFwillbereducedbythefractional quantity(1-FT),.whereFTis,tempering fraction(i.e.,diversion ofsomefractionofdischarge flowtotheintakecanalforthepurposeoftemperature control).
8+4%II'trf~x.C' 2.1.4Discussion 2.1.4.1ControlofLiquidEffluentBatchDischarges AtNineMilePointUnit1LiquidRadwasteEffluents arereleasedonly'nabatchmode.Topreventtheinadvertent releaseofanyliquidradwasteeffluents, radwastedischarge ismechanically isolated(blankflangeinstalled ordischarge valvechain-locked closed)following thecompletion ofabatchreleaseorseriesofbatchreleases.
,Thismechanical isolation remainsinplaceandwillonlyberemovedpriortothenextseriesofliquidradwastedischarges afterallanalysesrequiredinstationprocedures andTechnical Specification Table4.6.15-1A areperformed andmonitorsetpoints havebeenproperlyad]usted.
2.1.4.2Simultaneous Discharges ofRadioactive Liquids..'<<"If.duringthedischarge ofanyliquidradwastebatch,thereisanindication thattheservicewatercanalhasbecomecontaminated (throughaservicewatermonitoralarmorthroughagrabsampleanalysisintheeventthattheservicewatermonitorisinoperable) thedischarge shallbe.terminated immediately.
Theliquidradwastedischarge shallnotbecontinued untilthecauseoftheservicewateralarm(orhighgrabsampleanalysisresult)hasbeendetermined andtheappropriate corrective measurestakentoensure10CFR20,Appendix8,TableII,Column2(Technical Specification Section3.6.15.a(1))
limitsarenotexceeded.
ALi/A~
ALi/A~
2.1.4.3SamplingRepresentativenessThissectioncoversTechnicalSpecificationTable4.6.15-1Notebconcerningthoroughlymixing'feachbatchofliquidradwastepriortosampling.LiquidRadwasteTanksscheduledfordischargeatNineMilePointUnit1are'isolated(i.e;inletvalves:markedup)and.-at.leasttwo,tankvolumesofentrainedfluidsarerecirculatedpriortosampling.Minimumrecirculationtimeiscalculatedasfollows:-MinimumRecirculationTime2.0(T/R)Hhere:2.0Plantestablishedmixingfactor,unitlessTankvolume,galRecirculationflowrate,gpm.Additionally.theHiAlarmsetpointoftheLiquidRadwasteEffluentRadiationMonitorissetatavaluecorrespondingtonotmorethan--""'.70'Lof-~itscalculatedresponsetothegrabsampleorcorrespondingMPCvalues.Thus,thisradiationmonitorwillalarmifthegrabsample,orcorrespondingMPCvalue,issignificantlylowerinactivitythananypartofthetankcontentsbeingdischarged.
2.1.4.3SamplingRepresentativeness ThissectioncoversTechnical Specification Table4.6.15-1Notebconcerning thoroughly mixing'feachbatchofliquidradwastepriortosampling.
IWl*A'IO'"S~'omagr~'P(~,,~~~~i~)r+k'g4>i'I 2.1.4.4LiquidRadwasteSystemsOperationTechnicalSpecification3.6.16.arequiresthattheliquidradwastesystemshallbeusedtoreducetheradioactivematerialsinliquidwastespriortotheirdischarge,asnecessary,tomeettheconcentrationanddoserequirementsofTechnicalSpecification3.6.15.Utilizationof-theradwaste"systemwillbebasedonthecapabilityoftheindicatedcomponentsofeachprocesssystemtoprocesscontentsoftherespectivelowconductivityandhighconductivitycollectiontanks:1)LowConductivity(EquipmentDrains):RadwasteFilterandRadwasteDemin.(SeeFig.B-1)2)HighConductivity(FloorDrains):HasteEvaporator(seeFig.B-1)Cumulativedosecontributionsfromliquideffluentsforthecurrentl-'alendar'quarterandthecurrentcalendaryearshallbedeterminedasdescribedinSection2.3ofthismanualpriortothereleaseofeachbatchofliquidwaste.Thissamedosepro]ectionofSection2.3willalsobeperformedintheeventthatuntreatedliquidwasteis.discharged,toensurethat.thedoselimits'of.TechnicalSpecification3.6.15.a(2)arenotexceeded.(Therebyimplementingtherequirementsof10CFR50.36a,GeneralDesignCriteria60ofAppendixAandtheDesignOb)ectivegiveninSectionII-DofAppendixIto10CFR50).  
LiquidRadwasteTanksscheduled fordischarge atNineMilePointUnit1are'isolated (i.e;inletvalves:marked up)and.-at.leasttwo,tankvolumesofentrained fluidsarerecirculated priortosampling.
Minimumrecirculation timeiscalculated asfollows:-MinimumRecirculation Time2.0(T/R)Hhere:2.0Plantestablished mixingfactor,unitlessTankvolume,galRecirculation flowrate,gpm.Additionally.
theHiAlarmsetpointoftheLiquidRadwasteEffluentRadiation Monitorissetatavaluecorresponding tonotmorethan--""'.70'Lof-~itscalculated responsetothegrabsampleorcorresponding MPCvalues.Thus,thisradiation monitorwillalarmifthegrabsample,orcorresponding MPCvalue,issignificantly lowerinactivitythananypartofthetankcontentsbeingdischarged.
IWl*A'IO'"S~'omagr~'P(~,,~~~~i~)r+
k'g4>i'I 2.1.4.4LiquidRadwasteSystemsOperation Technical Specification 3.6.16.arequiresthattheliquidradwastesystemshallbeusedtoreducetheradioactive materials inliquidwastespriortotheirdischarge, asnecessary, tomeettheconcentration anddoserequirements ofTechnical Specification 3.6.15.Utilization of-theradwaste"system willbebasedonthecapability oftheindicated components ofeachprocesssystemtoprocesscontentsoftherespective lowconductivity andhighconductivity collection tanks:1)LowConductivity (Equipment Drains):RadwasteFilterandRadwasteDemin.(SeeFig.B-1)2)HighConductivity (FloorDrains):HasteEvaporator (seeFig.B-1)Cumulative dosecontributions fromliquideffluents forthecurrentl-'alendar
'quarterandthecurrentcalendaryearshallbedetermined asdescribed inSection2.3ofthismanualpriortothereleaseofeachbatchofliquidwaste.Thissamedosepro]ection ofSection2.3willalsobeperformed intheeventthatuntreated liquidwasteis.discharged, toensurethat.thedoselimits'of.Technical Specification 3.6.15.a(2) arenotexceeded.
(Therebyimplementing therequirements of10CFR50.36a, GeneralDesignCriteria60ofAppendixAandtheDesignOb)ective giveninSectionII-DofAppendixIto10CFR50).  
~P1"J~W+
~P1"J~W+
2.1.4.4(Cont'd)Forthepurposeofdosepro]ection,thefollowingassumptionsshallbemadewithregardto-concentrationsofnon-gammaemittingradionuclidessubsequentlyanalyzedoff-site:a)[H-3]>H-3Concentrationfoundrecentcondensatestoragetankanalysis.b)[Sr-89]>4xCs-137Concentrationc)[Sr-90]>0.5xCs-137Concentrationd)[Fe-55]>1xCo-60ConcentrationAssumedScalingFactorsusedinb,c,anddaboverepresentconservativeestimatesderivedfromanalysisofhistoricaldatafromprocesswastestreams.Followingreceiptofoff-siteH-3,Sr-89,Sr-90andFe-55analysisinformation,doseestimatesshallberevised---usingactualradionuclideconcentrationsandactualtankvolumesdischarged.
2.1.4.4(Cont'd)Forthepurposeofdosepro]ection, thefollowing assumptions shallbemadewithregardto-concentrations ofnon-gamma emittingradionuclides subsequently analyzedoff-site:
Fp,cyb)}I',t'i,j>p<,pgb~iwp4'"r*e'I 2.1.4.5ServiceWaterSystemContaminationServicewaterisnormallynon-radioactive.Ifcontaminationissuspected,asindicatedbya.significantincreaseinservicewatereffluentmonitorresponse,grabsampleswillbeobtainedfromtheservicewaterdischargelinesandagammaisotopicanalysismeetingtheLLOrequirementsofTechnicalSpecificationTable4.6.15-1completed.Ifit-'is-determined.thataninadvertentradioactivedischargeisoccurringfromtheservicewatersystem,then:a)A50.59safetyevaluationshallbeperformed(ref.IEEBulletin80-10),b)Oailyservicewatereffluentsamplesshallbetakenandanalyzedforprincipalgammaemittersuntilthereleaseisterminated,c)AnincidentcompositeshallbepreparedforH-'3,grossalpha,Sr-89,Sr-90andFe-55analysesandI-'d)"Ooseprojectionsshallbeperformed.inaccordancewithSection2.3ofthismanual(usingestimatedconcentrationsforH-3,Sr-89,Sr-90andFe-55tobeconservativelydeterminedbysupervisionatthetimeoftheincident).Additionally,servicewatereffluentmonitorsetpointsmayberecalculatedusingtheactualdistributionofisotopesfoundfromsampleanalysis.
a)[H-3]>H-3Concentration foundrecentcondensate storagetankanalysis.
1I~LgC4t*'AtttEI'E 2.2LiquidEffluentConcentrationCalculationThiscalculationdocumentscompliancewithTechnicalSpecificationSection3.6.1.5.a(1).Theconcentrationofradioactivematerialreleasedinliquideffluentstounrestrictedareas(seeFigureB-7)shallbelimitedtothe'concentrationsspecifiedin10CFR20,AppendixB,TableII,Column2,forradionuclidesotherthandissolvedorentrainednoblegases.Fordissolvedorentrainednoblegases,theconcentrationshallbelimitedto2E-4microcurie/milliliter(uCi/ml)totalactivity.TheconcentrationofradioactivityfromLiquidRadwastebatchreleasesand,ifapplicable,ServiceHaterSystemandemergencycondenserstart-upventdischargesareincludedinthecalculation.Thecalculationisperformedforaspecificperiodoftime.Nocredittakenforaveragingoverthecalendaryearaspermittedby10CFR20.106.Thelimitingconcentrationiscalculatedasfollows:~PCFrti"11<~s(("i/ml)is*Fs)/(Pi*Zs(FsHhere:HPCFractionThelimitingconcentrationof10CFR20,Appendix8,TableII,forradionuclidesotherthandissolvedorentrainednoblegases.Fornoblegases,theconcentrationshallbelimitedto2E-4microcurie/mltotalactivity.
b)[Sr-89]>4xCs-137Concentration c)[Sr-90]>0.5xCs-137Concentration d)[Fe-55]>1xCo-60Concentration AssumedScalingFactorsusedinb,c,anddaboverepresent conservative estimates derivedfromanalysisofhistorical datafromprocesswastestreams.Following receiptofoff-siteH-3,Sr-89,Sr-90andFe-55analysisinformation, doseestimates shallberevised---usingactualradionuclide concentrations andactualtankvolumesdischarged.
Fp,cyb)}I',t'i,j>p<,pgb~iwp4'"r
*e'I 2.1.4.5ServiceWaterSystemContamination Servicewaterisnormallynon-radioactive.
Ifcontamination issuspected, asindicated bya.significant increaseinservicewatereffluentmonitorresponse, grabsampleswillbeobtainedfromtheservicewaterdischarge linesandagammaisotopicanalysismeetingtheLLOrequirements ofTechnical Specification Table4.6.15-1completed.
Ifit-'is-determined.
thataninadvertent radioactive discharge isoccurring fromtheservicewatersystem,then:a)A50.59safetyevaluation shallbeperformed (ref.IEEBulletin80-10),b)Oailyservicewatereffluentsamplesshallbetakenandanalyzedforprincipal gammaemittersuntilthereleaseisterminated, c)Anincidentcomposite shallbepreparedforH-'3,grossalpha,Sr-89,Sr-90andFe-55analysesandI-'d)"Ooseprojections shallbeperformed
.inaccordance withSection2.3ofthismanual(usingestimated concentrations forH-3,Sr-89,Sr-90andFe-55tobeconservatively determined bysupervision atthetimeoftheincident).
Additionally, servicewatereffluentmonitorsetpoints mayberecalculated usingtheactualdistribution ofisotopesfoundfromsampleanalysis.
1I~LgC4t*'AtttEI'E 2.2LiquidEffluentConcentration Calculation Thiscalculation documents compliance withTechnical Specification Section3.6.1.5.a (1).Theconcentration ofradioactive materialreleasedinliquideffluents tounrestricted areas(seeFigureB-7)shallbelimitedtothe'concentrations specified in10CFR20,AppendixB,TableII,Column2,forradionuclides otherthandissolved orentrained noblegases.Fordissolved orentrained noblegases,theconcentration shallbelimitedto2E-4microcurie/milliliter (uCi/ml)totalactivity.
Theconcentration ofradioactivity fromLiquidRadwastebatchreleasesand,ifapplicable, ServiceHaterSystemandemergency condenser start-upventdischarges areincludedinthecalculation.
Thecalculation isperformed foraspecificperiodoftime.Nocredittakenforaveraging overthecalendaryearaspermitted by10CFR20.106.
Thelimitingconcentration iscalculated asfollows:~PCFrti"11<~s(("i/ml)is*Fs)/(
Pi*Zs(FsHhere:HPCFractionThelimitingconcentration of10CFR20,Appendix8,TableII,forradionuclides otherthandissolved orentrained noblegases.Fornoblegases,theconcentration shallbelimitedto2E-4microcurie/ml totalactivity.
IV@.1,,S'IlkWih~ptertI.gkA~~
IV@.1,,S'IlkWih~ptertI.gkA~~
2.2(Cont'd)(uCi/ml)iTheconcentrationofnuclideiinparticulariseffluentstreams,uCi/ml.FTheflowrateofaparticulareffluentstreams,gpm.MPCiThelimitingconcentrationofaspecificnuclideifrom.'10CFR20,Appendixb,Table-II,Column2(noblegaslimitis2E-4uCi/ml)X((uCi/ml)i*F)Thetotalactivityrateofnuclidei,inalleffluentstreamss,uCi/ml*gpm$(F)".Thetotalflowrateofalleffluentstreamss,gpm(includingthosestreamswhichdonotcontainradioactivity).AvalueoflessthanoneforMPCfractionisconsideredacceptableforcompliancewithTechnicalSpecificationSection3.6.15.a.(1).2.3DoseDetermination-,2.3.1,MaximumDoseEquivalentPathwayAdoseassessmentreportwaspreparedfortheNineMilePointUnit1facilitybyCharlesT.Main,Inc.,ofBoston,MA.Thisreportpresentedthecalculateddoseequivalentratestoindividualsaswell,asthe.,populationwithina50-mileradiusofthefacilitybasedontheradionuclidesreleasedin-liquid.and=gaseouseffluents-during.thetimeperiodsof1July1980through31December1980andfromJanuary1981through31December1981;Theradwasteliquid'releasesarebasedonacanaldi.schargerateof590ft/secwhichaffectsnearfieldandfarfielddilution;therefore,thisreportisspecifictothis.situation.Utilizingtheeffluentdatacontainedinthe12 rPAg4J<7 2.3.1(Cont'd)Semi-AnnualRadioactiveEffluentReleaseReportsassourceterms,doseequivalentratesweredeterminedusingtheenvironmentalpathwaymodelsspecifiedinRegulatoryGuides1.109and1.111asincorporatedintheNRCcomputercodesLADTAPforliquidpathways,andXOQDOQandGASPARforgaseouseffluentpathways.Doseequivalentrateswere-calculatedforthe'total'odyaswellassevenorgansand/ortissues---fortheadult,teen,child,andinfantagegroups.Fromthestandpointofliquideffluents,thepathwaysevaluatedincludedfishanddrinkingwateringestion,andexternalexposuretowaterandsediment.Themajorityofthedoseforaradwasteliquidbatchreleasewasreceivedviathefishpathway.However,tocomplywithTechnicalSpecificationsfordoseprojections,thedrinkingwaterandsedimentpathwaysareincluded.Therefore,alldosesdueto-liquideffluentsarecalculatedmonthlyforthefishanddrinkingwateringestionpathwaysandthesedimentexternalpathwayfromalldetectednuclides"<<inliquideffluentsreleasedtotheunrestrictedareastoeachorgan.Thedoseprojectionforliquidbatchreleaseswillalsoincludedischargesfromtheemergencycondenserventasapplicable,forallpathways.Eachagegroupdosefactor,Ait,isgivenintables1-1to1-8.Toexpeditetimethe,doseiscalculatedforamaximumindividualinsteadofeachagegroup.Thismaximumindividualwillbeacompositeofthehighestdosefactorofeachagegroupforeachorgan,henceAit.ThefollowingexpressionfromNUREG0133,Section4.3isusedtocalculatedose:Dtgi[Alt$1(dT1CilF1)]13  
2.2(Cont'd)(uCi/ml)i Theconcentration ofnuclideiinparticular iseffluentstreams,uCi/ml.FTheflowrateofaparticular effluentstreams,gpm.MPCiThelimitingconcentration ofaspecificnuclideifrom.'10CFR20, Appendixb,Table-II,Column2(noblegaslimitis2E-4uCi/ml)X((uCi/ml)i
*F)Thetotalactivityrateofnuclidei,inalleffluentstreamss,uCi/ml*gpm
$(F)".Thetotalflowrateofalleffluentstreamss,gpm(including thosestreamswhichdonotcontainradioactivity).
AvalueoflessthanoneforMPCfractionisconsidered acceptable forcompliance withTechnical Specification Section3.6.15.a.(1).
2.3DoseDetermination
-,2.3.1,MaximumDoseEquivalent PathwayAdoseassessment reportwaspreparedfortheNineMilePointUnit1facilitybyCharlesT.Main,Inc.,ofBoston,MA.Thisreportpresented thecalculated doseequivalent ratestoindividuals aswell,asthe.,population withina50-mileradiusofthefacilitybasedontheradionuclides releasedin-liquid.and=gaseous effluents-during.
thetimeperiodsof1July1980through31December1980andfromJanuary1981through31December1981;Theradwasteliquid'releases arebasedonacanaldi.scharge rateof590ft/secwhichaffectsnearfieldandfarfielddilution; therefore, thisreportisspecifictothis.situation.
Utilizing theeffluentdatacontained inthe12 rPAg4J<7 2.3.1(Cont'd)Semi-Annual Radioactive EffluentReleaseReportsassourceterms,doseequivalent ratesweredetermined usingtheenvironmental pathwaymodelsspecified inRegulatory Guides1.109and1.111asincorporated intheNRCcomputercodesLADTAPforliquidpathways, andXOQDOQandGASPARforgaseouseffluentpathways.
Doseequivalent rateswere-calculated forthe'total'ody aswellassevenorgansand/ortissues---
fortheadult,teen,child,andinfantagegroups.Fromthestandpoint ofliquideffluents, thepathwaysevaluated includedfishanddrinkingwateringestion, andexternalexposuretowaterandsediment.
Themajorityofthedoseforaradwasteliquidbatchreleasewasreceivedviathefishpathway.However,tocomplywithTechnical Specifications fordoseprojections, thedrinkingwaterandsedimentpathwaysareincluded.
Therefore, alldosesdueto-liquideffluents arecalculated monthlyforthefishanddrinkingwateringestion pathwaysandthesedimentexternalpathwayfromalldetectednuclides"<<inliquideffluents releasedtotheunrestricted areastoeachorgan.Thedoseprojection forliquidbatchreleaseswillalsoincludedischarges fromtheemergency condenser ventasapplicable, forallpathways.
Eachagegroupdosefactor,Ait,isgivenintables1-1to1-8.Toexpeditetime the,doseiscalculated foramaximumindividual insteadofeachagegroup.Thismaximumindividual willbeacomposite ofthehighestdosefactorofeachagegroupforeachorgan,henceAit.Thefollowing expression fromNUREG0133,Section4.3isusedtocalculate dose:Dtgi[Alt$1(dT1CilF1)]
13  
*W~hII+'Igc~4.
*W~hII+'Igc~4.
2.3.1(Cont'd)Nhere:OtThecumulativedosecommitmenttothetotalbodyoranyorgan,fromtheliquideffluentsforthetotaltimeperiod(dT1),mremdT1Thelengthofthe1thtimeperiodoverwhichCilandFlareaveragedforallliquidreleases,hoursCilTheaverageconcentrationofradionuclide,i,inundilutedliquideffluentsduringtimeperioddT1fromanyliquidrelease,uCi/mlAitThesiterelatedingestiondosecommitmentfactortothetotalbodyoranyorgantforeachidentifiedprincipalgammaorbetaemitterforamaximumindividual,mrem/hrperuCi/mlFlThenearfieldaveragedilutionfactorforCilduringanyliquideffluentrelease.Definedastheratioofthemaximumundilutedliquidwasteflowduringreleasetothe.averageflowfromthesitedischargestructuretounrestrictedreceivingwaters,unitless.Aitvaluesforradwasteliquidbatchreleasesatadischargerateof295ft/sec(onecirculatingwaterpumpinoperation)arepresentedintable's1-1to1-4.Aitvaluesforanemergencyiatcondenserventreleasearepresentedintables1-5to1-8.The'mergencycondenserventreleasesareassumedtotraveltotheperimeterdrainsystemandreleasedfromthedischargestructureatarateof.33ft/sec.SeeAppendixAforthedosefactorAit3derivation.Toexpeditetimethedoseiscalculatedtoamaximumindividual.Thismaximumindividualisa;composite'of-thehighest-."dosefactorAitofeachagegroupaforeachorgantandeachnuclidei.Ifanuclide"isdetectedforwhichafactorisnotlisted,thenitwillbecalculatedandincludedinarevisiontotheOOCN.
2.3.1(Cont'd)Nhere:OtThecumulative dosecommitment tothetotalbodyoranyorgan,fromtheliquideffluents forthetotaltimeperiod(dT1),mremdT1Thelengthofthe1thtimeperiodoverwhichCilandFlareaveragedforallliquidreleases, hoursCilTheaverageconcentration ofradionuclide, i,inundiluted liquideffluents duringtimeperioddT1fromanyliquidrelease,uCi/mlAitThesiterelatedingestion dosecommitment factortothetotalbodyoranyorgantforeachidentified principal gammaorbetaemitterforamaximumindividual, mrem/hrperuCi/mlFlThenearfieldaveragedilutionfactorforCilduringanyliquideffluentrelease.Definedastheratioofthemaximumundiluted liquidwasteflowduringreleasetothe.averageflowfromthesitedischarge structure tounrestricted receiving waters,unitless.
f0i~i4,e+$'a,,C'(<>>5Y"ztl$'~,
Aitvaluesforradwasteliquidbatchreleasesatadischarge rateof295ft/sec(onecirculating waterpumpinoperation) arepresented intable's1-1to1-4.Aitvaluesforanemergency iatcondenser ventreleasearepresented intables1-5to1-8.The'mergency condenser ventreleasesareassumedtotraveltotheperimeter drainsystemandreleasedfromthedischarge structure atarateof.33ft/sec.SeeAppendixAforthedosefactorAit3derivation.
2.3.1(cont'd)Alldosescalculatedinthismannerforeachbatchofliquideffluentwillbesummedforcomparisonwithquarterlyandannuallimits,addedtothedosesaccumulatedfromotherreleasesinthequarterandyearofinterest.Inallcases,thefollowingrelationshipswillhold:Foracalendarquarter:0t<1.5mremtotalbody0<5mremforanyorganForthecalendaryear:Ot<.3.0mremtotalbody0t<10mremforanyorgan-"<~where0'otal;dosereceivedduetoliquideffluentreleasestothetotalbodyoranyorgan,  
Toexpeditetimethedoseiscalculated toamaximumindividual.
+pvEp1e 2.3.1(Cont'd)Iftheselimitsareexceeded,aspecialreportwillbesubmittedto-'theNRCidentifying.the..cause,and,,proposedcorrectiveactions.Inaddition,iftheselimitsareexceededbyafactoroftwo,calculationsshallbemadetodetermineifthedoselimitscontainedin40CFR190havebeenexceeded.Doselimits,ascontainedin40CFR190aretotalbodyandorgandosesof25mremperyearandathyroiddoseof75mremperyear.=Thesecalculationswillincludedosesasaresultofliquidandgaseouspathwaysaswellasdosesfromdirectradiation.Theliquidpathwayanalysiswillonlyincludethefishandsedimentpathwayssincethedrinkingwaterpathwayisinsignificant.Thispathwayis.onlyincludedinthe.station'seffluentdoseprojectionstocomply'""withTechnicalSpecifications.Liquid,gaseousanddirectradiation.pathwaydoseswillconsidertheJamesA.FitzPatrickandNineMilePointUnitIIfacilitiesaswellasNineMilePointUnitINuclear.Station.Intheeventthecalculationsdemonstratethatthe40CFR190doselimits,asdefinedabove,havebeenexceeded,thenareportshallbepreparedandsubmittedtotheCommissionwithin30daysasspecifiedinSection3.6.15.doftheTechnicalSpecifications.I'"",i.'Section,4.,0'oftheODCMcontainsmoreinformationconcerningcalculationsforanevaluationofwhether40CFR190limitshavebeenexceeded.
Thismaximumindividual isa;composite'of
I.~01C.aI*)It1l'E 3.0GASEOUSEFFLUENTS3.1SetpointDeterminations3.1.1Basis~~Stackgasandoffgasmonitorsetpointswillbeestablishedsuchthattheinstantaneousreleaserateofradioactivematerialsingaseouseffluentsdoesnotexceedthe10CFR20limitsforannualrelease.rate.Thesetpointswillbeactivatediftheinstantaneousdoserateator-beyondthe(land)site'boundarywould.exceed500mrem/yr,to.the..wholebodyor3000mrem/yrtotheskinfromthecontinuousreleaseofradioactivenoblegasinthegaseouseffluent.Emergencycondenserventmonitorsetpointswillbeestablishedsuch"thatthereleaserateforradioactivematerialsingaseouseffluentsdonotexceedthe10CFR20limitsforannualreleaserateovertheprojectedlongestperiodofrelease.Monitorsetpointsfromcontinuousreleasepointswillbedeterminedonceperquarterundernormalreleaserateconditionsandwillbebasedon'the'isotopiccompositionoftheactualreleaseinprogress,oranoffgasisotopicdistributionoramoreconservativedefaultcompositionspecifiedinthepertinentprocedure.Ifthecalculatedsetpointtshigherthantheexistingsetpoint,itisnotmandatorythatthesetpointbechanged.Monitorsetpointsforemergencycondenserventmonitorsareconservativelyfixedat5mr/hrforreasonsdescribedinSections3.1.4andthereforedonotrequireperiodicrecalculations.Underabnormalsitereleaserateconditions,monitor.alarmsetpoints.fromcontinuousreleasepointswillberecalculatedand,ifnecessary,resetatmorefrequentintervalsasdeemednecessaryby.CORMSupervision.Inparticular,contributionsfrombothJAFandNMP-2andtheEmergencyCondenserVentsshallbeassessed:"Duringoutagesanduntilpower.operationisagainrealized,thelastoperatingstackandoffgasmonitoralarmsetpointsshallbeused.
-thehighest-."
k7i'tZF<~P 3.1.1(Cont'd)Sincemonitorsrespondtonoblegasesonly,monitoralarmpointsaresettoalarmpriortoexceedingthecorrespondingtotalbodydose'rates.Theskindoseratelimitisnotusedinsetpointcalculationsbecauseitisneverlimiting.3.1..2,StackMonitorSetpointsThedetailedmethodsforestablishingsetpointsshallbecontainedinthestationprocedures.Thesemethodsshallapplythefollowinggeneralcriteria:(1)RationaleforStackmonitorsettingsisbasedonthegeneralequation:releaserateactualcorrespondingdoserate,actualreleaseratemax.allowablecorrespondingdoserate,max.allowable()max500mrem/yrwhere:Vireleaserateforeachisotopei,uCi/secgamma'holebodydosefactorinunitsofmrem/yrperuCi/sec(SeeTable3-2)(Q)maxinstantaneousreleaseratelimituCi/sec18  
dosefactorAitofeachagegroupaforeachorgantandeachnuclidei.Ifanuclide"is detectedforwhichafactorisnotlisted,thenitwillbecalculated andincludedinarevisiontotheOOCN.
+a'v'1~IIQ%l''tl 3.1.2(Cont'd)(2)Toensurethat10CFR20andTechnicalSpecificationsdoseratelimitsarenotexceeded,thehihialarmsonthestackmonitorsshallbesetlowerthanorequalto(0.9)(Q).Hialarmsmax'hallbesetlowerthanorequalto(0.5)(Q)max'3)Basedontheaboveconservatism,thedosecontributionfromJAFandNMP-2canusual,lybeignored..DuringEmergencyClassificationsatJAForNMP-2duetoairborneeffluent,orafteremergency.condenservent;releases.of-significantproportions,the500mrem/yrvaluemaybereducedaccordingly.(4)ToconvertmonitorgrosscountratestouCi/secreleaserates,thefollowinggeneralformulashallbeapp'lied:(C-B)KQuCi/secreleaseratewhere:'BKsCmmonitorgrosscountrateincpsorcpm;cpscountspersecond,cpmcountsperminutemonitorbackgroundcountratestackmonitorefficiencyfactorwithunitsofuCi/sec-cpsoruCi/sec-cpm(5)MonitorKfactorsshallbedeterminedusingthegeneralformula:KQiQi/(C-8)where:individualradionuclidestackeffluent.releaserateasdeterminedbyisotopicanalysis.Kfactorsmoreconservativethanthosecalculatedbythe-abovemethodologymaybeassumed.-19  
f0i~i4,e+$'a,,C'(<>>5 Y"ztl$'~,
,bt'4r~II4U 3.1.2(Cont'd)Alternatively,whenstackreleaseratesarenearthelowerlimitofdetection,thefollowinggeneralformulamaybeused.tocalculatek:1/KsE~(ii~kYkEk)3.7E4dff'-uCiwhere:fstackflowincc/secEefficiencyinunitsofcpm-cc/uCiorcps-cc/uCi(cpmcountsperminute;cpscountspersecond)Ekcpm-cc/bpsorcps-cc/psFromenergycalibrationcurveproducedduringNBStraceableprimarygascalibrationortransfersourcecalibration(bpsbetapersecond;psgammaspersecond)Ykb/d(betas/disintegration)orV/d(gammas/d)FiActivityfractionofnuclideiinthemixtureinuclidecounterk.discreteenergybetaorgammaemitterpernuclidecountersi~secondsThismonitorcalibrationmethodassumesanoblegasdistributiontypicalofarecoilreleasemechanism.Toensurethatthecalculatedefficiencyisconservative,betaorgammaemissionswhoseenergyisabovetherangeofcalibrationofthedetectorarenotincludedinthecalculation.
2.3.1(cont'd)Alldosescalculated inthismannerforeachbatchofliquideffluentwillbesummedforcomparison withquarterly andannuallimits,addedtothedosesaccumulated fromotherreleasesinthequarterandyearofinterest.
Q}4 3.1.3Recomb)nerDischarge<DffGas)MonitorSetpoints(1)Thehihialarmpointsshallactivatewithrecombinerdischargeratesequaltoorlessthan500,000uCi/sec.Thisalarmpointmaybesetequal-.toorlessthan1Ci/secforaperiodoftimeInottoexceed60daysprovidedtheoffgastreatmentsystemisinoperation.(2)Thehialarmpointsshallactivatewithrecombinerdischargeratesequaltoorlessthan500,000uCi/sec(3)ToconvertmonitormR/hrreadingstouCi/sec,theformulabelowshallbeapplied:<R)(KR)QRuCi/secrecombinerdischargereleaserate"where:RmR/hrmonitorindicatorKRefficiencyfactorinunitsofuCi/sec/mR/hrdeterminedpriortosettingmonitoralarmpoints(4)MonitorKRfactorsshallbedeterminedusingthegeneralformula:KRQi/Rwhere:Qi-individualradionucliderecombinerdischargereleaserateasdeterminedbyisotopicanalysisandflowratemonitor.KRfactorsmoreconservativethanthosecalculatedbytheabovemethodologymaybeassumed.
Inallcases,thefollowing relationships willhold:Foracalendarquarter:0t<1.5mremtotalbody0<5mremforanyorganForthecalendaryear:Ot<.3.0mremtotalbody0t<10mremforanyorgan-"<~where0'otal;dose receivedduetoliquideffluentreleasestothetotalbodyoranyorgan,  
J4jCIf4/Qi'lag'I~ppAl 3.1.3(Cont'd)(5)Thesetpointschosenprovideassurancethatthetotalbodyexposuretoanindividualattheexclusionareaboundarywillnotexceedaverysmallfractionofthelimitsof10CFRPart100intheeventthiseffluentisinadvertentlydischargeddirectlytotheenvironmentwithouttreatment(therebyimplementingtherequirementsofGeneralOesignCriteria60and64ofAppendixAto10CFRPart,50)..Additionally,thesesetpointsserveto,limitbuildupoffissionproductactivitywithinthestation.systemswhichwouldresultifhighfuelleakageweretobepermittedoverextendedperiods.3.1.4EmergencyCondenserVentHonitorSetpointThemonitorsetpointwasestablishedbycalculation("Emergency,CondenserVentHonitorAlarmSetpoint",January13,1986,NHPCFileCode&#xb9;'l61*99).Assumingahypotheticalcasewith(1)reactorwatertiodineconcentrationshigherthantheTechnicalSpecificationLimit,(2)reactorwaternoblegasconcentrationshigherthanwouldbeexpectedatTechnicalSpecificationiodinelevels,and(3)leakageofreactorsteamintotheemergencycondensershellat300'Aofratedflow(or1.3E6lbs/hr),thecalculationpredictsanemergencycondenserventmonitorresponseof20mR/hr.Suchareleasewouldresultinlessthan'0CFR20.doseratevaluesatthesiteboundaryandbeyondfortypical"emergencycondensercooldownperiods.Sincea20mR/hrmon'itorresponsecan,intheory,beachievableonlywhenreactorwateriodinesarehigherthanpermittedbyTechnicalSpecifications,aconservativemonitorsetpointof5mr/hrhasbeen-adopted.
+pvEp1e 2.3.1(Cont'd)Iftheselimitsareexceeded, aspecialreportwillbesubmitted to-'theNRCidentifying
IICof~hVWII,aITWIr'Tr~'t.ITl\ITttI0 3.1.5Discussion3.1.5.1StackEffluentMonitoringSystemDescription-TheNMP-1Stack'EffluentaMonitoringSystemconsistsoftwosubsystems;theRadioactiveGaseousEffluentMonitoringSystem(RAGEMS)andtheoldGeneralElectricStackMonitoringSystem(OGESMS).Duringnormaloperation,theOGESMSshallbeusedtomonitorstationnoble'aseffluentsandcollectparticulatesandiodinesamplesincompliancewithTechnicalSpecificationrequirements.TheRAGEMS.isdesignedtobepromptlyactivatedfromtheMainControl"RoomforuseinhighrangemonitoringduringaccidentsituationsincompliancewithNUREG0737criteria.OverallsystemschematicfortheOGESMSandRAGEMSareshownonFigureB-9.AsimplifiedviewofRAGEMSShowingUnit0,1,2,3and4canbefoundonFigureB-S.TheRAGEMScanprovidecontinuousaccidentmonitoringandon-lineisotopicanalysisofNMP-1stackeffluentnoblegasesatLowerLevelsofDetectionlessthanTechnicalSpecificationTable4.6.15-2limits.Activitiesaslowas5.0E-Bandashighas2.0E5uCi/ccfornoblegasesaredetectablebythesystem.
.the..cause,and,,proposed corrective actions.Inaddition, iftheselimitsareexceededbyafactoroftwo,calculations shallbemadetodetermine ifthedoselimitscontained in40CFR190havebeenexceeded.
i&jan"JP~.0-y~yII~*'Iletgledbl4II 3T.5.2StackSampleflowPath-RAGEHS'"Theeffluentsampleisobtainedinsidethestackatelevation530'singanisokineticprobewithfourorifices.Thesamplelinethenbendsradiallyoutandbackintothestack;descendsdownthestackandoutofthestack-atapproximatelyelevation257';runshorizontally(enclosedinheattracing)some270'longtheoffgas.tunnel;andenterstheRAGEHSlocatedontheTurbineBuilding250'Dilutioncabinet-Unit0)andOffGasBuilding247'Particulate,Iodine,NobleGasstations-Units1-3).'Inthe'Dilutioncabinet'oftheRAGEHS,thestackgasmaybedilutedduringaccidentsituationsapproximately100-200X(firststage)or10000-40000X(firstandsecondstage)withgaseousnitrogensuppliedfromanon-siteliquidnitrogenstoragetank(seeFigure8-9).FromUnit0,thesamplegasentersUnit1-3ofRAGEHSandflowsthruin-lineparticulateandiodinecartridgesandthenthrueithera6liter(lowrange)or30cc(highrange)noblegaschamber.ThesamplegasnextflowsbackthruUnit0andtheoffgastunnel;andbackintothestack.
Doselimits,ascontained in40CFR190aretotalbodyandorgandosesof25mremperyearandathyroiddoseof75mremperyear.=Thesecalculations willincludedosesasaresultofliquidandgaseouspathwaysaswellasdosesfromdirectradiation.
I1+4gVL41wpfTJ'1SktI' 3.1.5.3StackSampleFlowPath-OGESHSTheOGESHSsampleisobtainedfromthesamestacksampleprobeastheRAGEHS.Fromtheexitofthestackatelevation257',thesamplelinerunseastapproximately20'ndthenverticallyapproximately8'otheOGESMSskid.IntheOGESMS,sampleflowsthruaparticuate/,.iodinecartridgehousingand.fournoblegasscintillationdetectors(i.e..07and08lowrange-betadetectorsandRN-03AandRN-038highrangegammadetectors).FromOGESHS,thestacksampleflowsbackintothestackatapproximatelyelevation257'.AllOGESMSdetectoroutputsaremonitoredandrecordedremotelyintheHainControlRoom.AlarmingcapabilitiesareprovidedtoalertOperatorsofhighreleaserateconditionspriortoexceedingTechnicalSpecification3.6.15.b(1)adoseratelimits.,StackparticulateandiodinesamplesareretrievedmanuallyfromtheOGESMSandanalyzedinthelaboratoryusinggammaspectroscopyatfrequenciesandLLOsspecifiedinTable4.6.15-2oftheTechnicalSpecifications.
Theliquidpathwayanalysiswillonlyincludethefishandsedimentpathwayssincethedrinkingwaterpathwayisinsignificant.
I'tI*P'tF 3.1.5.4SamplingFrequency/SampleAnalysisRegardlessofwhichstackmonitoringsubsystemisutilized,radioactivegaseous"wastes.shallbesampledandanalyzedinaccordancewiththesamplingandanalysisprogramspecifiedinTechnicalSpecificationTable4.6.15-2.Particulatesamplesaresavedandanalyzedforprincipalgammaemitters,grossalpha,Fe-55,Sr-89,Sr-90atmonthlyintervalsminimally.Thelatterthreeanalysesareperformedoff-sitefromacompositesample.Sampleanalysisfrequenciesareincreasedduringelevatedreleaserateconditions,followingstartup,shutdownandinconjunctionwitheachdrywellpurge.ConsistentwithTechnicalSpecificationTable4.6.15-2,stackeffluenttritiumissampledmonthly,duringeachdrywellpurge,and.weeklywhenfuelisoffloadeduntilstablereleaseratesaredemonstrated.Samplesareanalyzedoff-site.Linelosscorrectionfactorsareappliedtoallparticulateand"*"i,iodine.results.-Correctionfactorsof2.0and1.5areusedfordataobtainedfromRAGEHSandOGESHSrespectively.ThesecorrectionfactorsarebasedonempiricaldatafromsamplingconductedatNHP-1in1985(memofromJ.BlasiaktoRAGEHSFile,1/6/86,"StackSampleRepresentativenessStudy:RAGEHSvs.In-StackAuxiliaryProbeSamples").  
Thispathwayis.onlyincludedinthe.station's effluentdoseprojections tocomply'""withTechnical Specifications.
~k(1I~'i 3.1.5.5I-133EstimatesMonthly,thestackeffluentshallbesampledforiodinesovera24hourperiod-andtheI-135/I-131,andtheI-133/I-131ratioscalculated.TheseratiosshallbeusedtocalculateI-133,I-135releaseforlongeracquisitionsamplescollectedduringthemonth.Additionally,theI-135/I-131andI-133/I-131ratiosshouldalsobedeterminedafterasignificantchange-intheratioissuspected(eg,plantstatuschangesfromprolongedshutdowntopoweroperationorfueldamagehasoccurred).3.1.5.6GaseousRadwasteTreatmentSystemOperationTechnicalSpecification3.6.16.brequiresthatthegaseousradwastetreatmentsystemshallbeoperableandshallbeusedtoreduceradioactivematerialsingaseouswastepriortotheirdischargeasnecessarytomeettherequirementsofTechnicalSpecification3.6.15.b.ToensureTechnicalSpecification3.6.15.blimitsarenotexceeded,andtoconfirmproperradwastetreatmentsystemoperationasapplicable,cumulativedosecontributionsforthecurrentcalendarquarterandcurrentcalendaryearshallbedeterminedmonthlyinaccordancewithsection3.2ofthismanual.Initialdosecalculationsshallincorporate.thefollowing-assumptionswith,regardtoreleaseratesofnon-gammaemittingradionuclidessubsequentlyanalyzedoff-site:  
Liquid,gaseousanddirectradiation.
$l4gP">>'"wh'w'N~y'~~~'oi"pt, 3.1.5.6(Cont'd)a)H-3releaserate24uCi/secb)Sr-89releaserateZ4xCs-137releaseratec)Sr-90releaserateZ0.5xCs-137releaserated)Fe-55releaserate21xCo-60releaserateAssumedreleaseratesrepresentconservativeestimatesderivedfromanalysisofhistoricaldatafromeffluentreleasesandprocesswastestreams(SeeNAP34023,C.HaretoJ.Blasiak,April29,1988,"DoseEstimatesforBeta-EmittingIsotopes").Followingreceiptofoff-siteH-3,Sr-89,Sr-90,,Fe-55analysisinformation,doseestimatesshallberevisedusingactualradionuclideconcentrations.3.2DoseandDoseRateDeterminationsInaccordancewithspecifications4.6.15.b.(1),4.6.15.b.(2),and4.6.15.b.(3)doseanddoseratedeterminationswillbemademonthlytodetermine:(1)TotalbodydoseratesandgammaairdosesatthemaximumX/Q'landsectorsiteboundaryinterfaceandbeyond.(2)Skindoseratesandbetaairdosesatthe.maximumX/Qlandsectorsite'boundaryinterfaceandbeyond.(3)ThecriticalorgandoseanddoserateatthemaximumX/Qlandsectorsiteboundaryinterfaceandatacriticalreceptorlocationbeyondthesiteboundary..28  
pathwaydoseswillconsidertheJamesA.FitzPatrick andNineMilePointUnitIIfacilities aswellasNineMilePointUnitINuclear.Station.Intheeventthecalculations demonstrate thatthe40CFR190doselimits,asdefinedabove,havebeenexceeded, thenareportshallbepreparedandsubmitted totheCommission within30daysasspecified inSection3.6.15.doftheTechnical Specifications.
'pEv 3.2(Cont'd)Averagemeteorologicaldata(ie,maximumfiveyearannualaverageX/QandD/Qvaluesinthecaseofelevatedreleasesor1985annualaverageX/QandD/Qvalues,inthecaseofgroundlevelreleases)shallbeutilizedfordoseanddoseratecalculations.Whereaveragemeteorologicaldataisassumed,doseanddoseratesduetonoblegasesatlocationsbeyondthesiteboundarywillbelowerthanequivalentsiteboundarydose-anddoserates.Therefore,undertheseconditions,calculationsofnoblegasdoseanddoseratesbeyondthemaximumX/Qlandsectorsiteboundarylocationscanbeneglected.Thefrequencyofdoseratecalculationswillbeupgradedwhenelevatedreleaserateconditionsspecifiedinsubsequentsections3.2.1.1and3.2.1.2arerealized.rEmergencycondenserventreleasecontributionstothemonthlydoseanddoseratedeterminationswillbeconsideredonlywhentheemergencycondenserreturnisolationvalveshavebeenopenedforreactorcooldownorifEmergencyCondensertubeleaksdevelopwithorwithoutthesystem'sreturnisolationvalveopened.Withouttubeleakageoropeningofthereturnisolationvalves,releasesfromthissystemarenegligibleandthecorrespondingdosecontributionsdonothavetobeincluded.I I*me'q<a<~"<~,q"".'ltFgv, 3.2(Cont'd)Hhenreleasesfromtheemergencycondenserhaveoccurred,doserateanddosedeterminationsshall'beperformedusingmethodologyin3.2.1and3.2.2.Furthermore,environmentalsamplingmayalsobeinitiatedtorefineanyactualcontributiontodoses.SeeSection3.4.Criticalorgandoses.anddoseratesmaybeconservativelycalculated..byassuming.theexistenceofamaximumindividual.Thisindividualisacompositeofthehighestdosefactorofeachagegroup,foreachorganandtotalbody,andeachnuclide.ItisassumedthatallpathwaysareapplicableandthehighestX/Qand/or0/QvalueforactualpathwaysasnotedinTable3-1areineffect.Themaximumindividual'sdoseisequaltothesamedosethatpersonwouldreceiveiftheyweresimultaneouslysub]ectedtothehighestpathwaydoseateachcriticalreceptoridentifiedforeachpathway.Thepathwaysincludegrass-(cowandgoat)-milk,grass-cow-meat,vegetation,groundplaneandinhalation.TocomplywithTechnicalSpecificationswewillcalculatethemaximumindividualdoserateatthesiteboundaryand"'eyondatthecriticalresidence.Ifdoseordoseratescalculated,usingtheassumptionsnotedabove,reachTechnicalSpecificationlimits,actualpathwayswillbeevaluated,anddose/doseratesshallbecalculatedatseparatecriticalreceptorlocationsandcomparedwithapplicablelimits.30 ekedAI6'ltIII, 3.2.1DoseRate'ose'rateswillbe-calculated.monthly,ataminimum,orwhentheHi-Histackmonitoralarmsetpointisreached,todemonstratethatdoseratesresultingfromthereleaseofnoblegases,tritium,iodines,andparticulteswithhalflivesgreaterthan8daysare'ithinthelimitsspecifiedinlOCFR.20.Theselimitsare:NobleGasesHholeBodyDoseRate500mrem/yrSkinDoseRate3000mrem/yrTritiumIodinesandParticulatesOrganDoseRate1500mrem/yr3.2.1.1NobleGasesThefollowingnoblegasdoserateequationincludesthecontributionfromthestack(s)elevatedreleaseandtheemergencycondenservent(v)groundlevelreleasewhenapplicable(See.section3.2).31 Pf~
I'"",i.'Section, 4.,0'oftheODCMcontainsmoreinformation concerning calculations foranevaluation ofwhether40CFR190limitshavebeenexceeded.
fortotalbodydoserates(mrem/sec):ORg(mrem/sec)-3.17E-8Zi.[ViQi,+Ki(X/Q)Qi]i''iis'vivForskindoserates(mrem/sec):OR~+8(mrem/sec)-3.17E-8Zi[(Li(X/Q)s+1.118i)Qis+(Li+1.11Ni)<X/Q)vQiv~where:OR~totalbodygammadoserate(mrem/sec).OR~+6skindoseratefromgammaandbetaradiation(mrem/sec).=='he.constant,accountingforthegammawholebodydoseratefromstackradiation,foranelevatedfiniteplumereleasesforeachidentifiednoblegasnuclide,i.ListedonTable3-2inmrem/yrperuCi/sec..Kitheconstantaccountingforthegammawholebodydoseratefromimmersioninthesemi-infinitecloudforeachidentifiednoblegasnuclide,i.ListedinTable3-3inmrem/yrperuCi/m3(fromReg.Guide1.109)Qithereleaseofisotopei;(uCi;sstack,vvent).X/Q-therelativeplumeconcentration<inunitsofsec/m3)atthelandsectorsiteboundaryorbeyond.'Averagemeteorologicaldata(Table3-1)isused.'"Elevated"X/Qvaluesareusedforstackreleases(s",'stack);"Ground"X/QvaluesareusedforEmergencyCondenserVentreleases(vvent).theconstantaccountingforthebetaskindoseratefromimmersioninthesemi-infinitecloudforeachidentifiednoblegasnuclide,i.ListedinTable3-3:inmrem/yrperuCi/m3(fromReg.Guide1.109),.theconstant.accountingfor,the'airgammaradiationfromtheelevatedFiniteplumeresultingfromstackreleasesforeachidentifiednoblegasnuclide,i.ListedinTable3-2inmrad/yrperuCi/sec.Hitheconstantaccountingforthegammaairdoseratefrom-immersioninthesemi-infinitecloudforeachidentifiednoblegasnuclide,i.ListedinTable3-3inmrem/yrperuCi/m3(fromReg.Guide1.109)SeeAppendix8forderivationofBi,andVi.32 srfP.Ag<
I.~01C.aI*)It1l'E  
3.2.1.2Tritium,lodinesandParticulatesToensurethatthe'500'mrem/yearsitedoseratelimitisnotexceeded,offsitedoseratesfortritium,iodineandparticulateswithhalflivesgreaterthan8daysshallbecalculatedmonthlyandwhenreleaserates(Q).exceed0.34uCi/secusingthefollowingequation.Oak(mrem/sec)3.17E-8$~(~iRijak[Wsis+WvivWhere:oakTotaldosetoeachorgankofanindividualinagegroupa(mrem/sec).dispersionparametereitherX/Q(sec/m3)or0/Q(1/m2)dependingonpathwayandreceptorlocationassumed.Averagemeteorologicaldatais"used(Table3-1)."Elevated"W~valuesareusedforstackreleases(sstack);"Ground"WgvaluesareusedforEmergencyCondenserVentreleases(vvent).QiRi]ak3.17E-.Sthetotalquantityofisotopeireleased,(uCi/sec;sstack,vvent)thedosefactorforeachisotopei,pathway],agegroupa,andorgank(Table3-4,through3-22;m2-mrem/yrperuCi/secforallpathwaysexceptinhalation,mrem/yrperuCl/m3.theinverseofthenumberofsecondsinayear.,TheR.valuescontainedinTables3-4through3-22.werecalculatedusingthemethodologydefinedinNUREG-0133andparametersfromRegulatoryGuide1.109,Revision1;aspresentedinAppendixC.When-thereleaserateexceeds0.34uCi/sec,thedoserateassessmentshallalsoincludeJAFandNMP-2contribution.33 Pp4SA+v,1<
 
Theuseofthe0.34uCi/secreleaseratethresholdtoperformdoseratecalculationsisjustifiedasfollows:(a)The1500mrem/yrorgandoseratelimitcorrespondstoaminimumreleaseratelimitof0.34uCi/seccalculatedusingtheequation:1500(Q/sec)x(Ri)N))where:1500siteboundarydoseratelimit(mrem/year)(Ri]"])maxthemaximumcurie-to-doseconversionfactorequalto4.45E3mrem-sec/uCi-yrforSr-90,childboneatthecriticalresidencereceptorlocationbeyondthesiteboundary.(b)Theuseof0.34uCi/secreleaseratethresholdandthe4.45E3mrem-sec/uCi-yrcurie-to-doseconversionfactorisconservativesincecurie-to-doseconversionfactorsforotherisotopeslikelytobepresentaresignificantlylower.
==3.0 GASEOUSEFFLUENTS==
bfIs'4 3.2.2Dose-Calculationswillbeperformed.monthlyataminimum,.todemonstratethatdosesresultingfromthereleaseofnoblegases,tritium,iodines,andparticulateswithhalflivesgreaterthan8daysarewithinthelimitsspecifiedin10CFR50,AppendixI.Theselimitsare:NobleGases5mRgamma/calendarquarter'0mradbeta/calendarquarter10mRgamma/calendaryear'0mradbeta/calendaryearTritiumIodinesandParticulates7.5mremtoanyorgan/calendarquarter15mremtoanyorgan/calendaryear l+%i'Id4II'PtI1' 3.2.2.1NobleGasAirDoseThefollowingNobleGasairdoseequationincludescontributionsfromthestack(s)elevated.release.andtheemergencycondenservent(v)groundlevelreleasewhenapplicable(seesection3.2):Forgammaradiation.(mrad):Dg(mrd)317E8~iHi(XQ)vQiv+BiQisForbetaradiation(mrad):08(mrad)3.17E-SX)Ni(XQ)viv+siswhere:0ygammaairdose(mrad)0>betaairdose(mrad)theconstantaccountingfortheairgammaradiationfromtheelevatedfiniteplumeresultingfromstackreleasesforeachidentifiednoblegasnuclide,i.ListedinTable3-2inmrad/yr,peruCi/sec.NiTheconstantaccountingfortheairbetadosefromimmersioninthesemi-infinitecloudforeachidentifiednoblegasnuclide,i.ListedonTable3-3inmrad/yrperuCi/m3(fromReg.Guide1.109).Qithetotalquantityofisotopeireleased,(uCi/sec.)NotethattheunitsforthegammaairdoseareinmradcomparedtotheunitsforthelimitsareinmR.TheNRCrecognizesthat1mR1mrad,forgammaradi'ation.36 4q(gi 3.17E-Stheinverseofthenumberofsecondsinayear.theconstantaccountingfortheairgammadosefromimmersioninthesemi-infinitecloudforeachidentifiednoblegasnuclide,i.ListedonTable3-3inmrad/yrperuCi/m3<fromReg.Guide1.109).Allotherparametersareasdefinedinsection3.2.1.1.3.2.2.2Tritium,IodinesandParticulates'oensurethatthe15mrem/yrfacilitydoselimitisnotexceeded,offsitedosesfortritium,iodines,andparticulateswithhalflivesgreaterthan8daysshallbecalculatedmonthlyusingthefollowing.<<equation:0ak(mrem)3.17E-8Z~(SiRi]akWsis+WvivWhere:0akWgQiRi~ak3.17E-8Totaldosetoeachorgankofanindividualinagegroupa(mrem).dispersionparametereitherX/Q(sec/m3)or0/Q(1/m2)dependingonpathwayandreceptorlocationassumed.Averagemeteorologicaldataisused(Table3-1)."Elevated"W~valuesareused.forstackreleases(sstack);"Ground"W~valuesareusedforEmergencyCondenserVentreleases(vvent).thetotalquantityofisotopeireleased,<uCi/sec;s-stack,vvent)thedosefactorforeachisotopei,pathway],agegroupa,andorgank(Tables3-4,through3-22;m2-mrem/yrperuCi/sec)'theinverseofthenumberofsecondsinayear37 fII~0hlyCE' TheRvaluescontainedinTables3-4through3-22werecalculatedusingthemethodologydefinedinNUREG-0133andparametersfromRegulatoryGuide1.109,Revision1;aspresentedinAppendixC.3.2.2.3AccumulatingDosesDoseswillbecalculatedmonthly,ataminimum,forgammaair,betaair,andthecriticalorganforeachagegroup.Doseestimateswill,also,becalculatedmonthlypriortoreceiptofanyoffsiteanalysisdatai.e.,strontium,tritium,andiron-55.Resultswillbesummedforeachcalendarquarterandyear.Thecriticaldosesarebasedonthefollowing:noblegasplumeairdosedirectradiationfromgroundplanedepositioninhalationdosecowmilkingestiondosegoatmilkingestiondose'cowmeatingestiondosevegetation(foodcrops)ingestiondoseThequarterlyandannualresultsshallbecomparedtothelimitslistedinparagraph,3.2.2.If,thelimitsareexceeded,specialreports,asrequiredbySection6.9.3oftheTechnical-Specification,shallbesubmitted.38 A~"I 3.3CriticalReceptorsInaccordancewiththeprovisionsof10CFR20and10CFR50,AppendixI,thecriticalreceptorshavebeenidentifiedandare"containedinTable3-1.Forelevatednoblegasreleasesthecriticalreceptoristhesiteboundary.Hhen1985averageannualX/Qvaluesareusedforgroundlevelnoblegasreleases,thecriticalreceptoristhemaximumX/Qlandsectorsiteboundaryinterface.Fortritium,iodines,andparticulateswithhalflivesgreaterthaneightdays,thecriticalpathwaysaregrass-(cowandgoat)-milk,grass-cowmeat,vegetation,inhalationanddirectradiation(groundplane)asaresultofgrounddeposition.Thegrass-(cowandgoat)-milk,andgrass-cow-meatpathwayswillbebasedonthegreatest0/Qlocation.Thislocationhasbeendeterminedincon]unctionwiththelandusecensus(technicalspecification3.6.22)andissub]ecttochange.Thevegetation(foodcrop)pathwayisbasedonthegreatest0/Qgardenlocationfromwhich,samplesaretaken.Thislocationmayalsobemodifiedasaresultof-vegetationsamplingsurveys.39  
3.1SetpointDeterminations 3.1.1Basis~~Stackgasandoffgasmonitorsetpoints willbeestablished suchthattheinstantaneous releaserateofradioactive materials ingaseouseffluents doesnotexceedthe10CFR20limitsforannualrelease.rate.Thesetpoints willbeactivated iftheinstantaneous doserateator-beyondthe(land)site'boundary would.exceed500mrem/yr,to.the..wholebodyor3000mrem/yrtotheskinfromthecontinuous releaseofradioactive noblegasinthegaseouseffluent.
$*PC4gi+1 3.3(Cont'd)TocomplywithTechnicalSpecifications,theinhalationandground'lanedosepathwayswill.be.,calculatedatthesiteboundaryandbeyondatthecriticalresidence.BecausetheTechnicalSpecificationsstatetocalculate"atthesiteboundaryandbeyond",insteadof"atthesiteboundaryorbeyond",suchasUnit2,thedosesand/ordoseratesmustbecalculatedforamaximumindividualwhoisexposedtoallpathwaysatthesiteboundaryandatthecriticalresidence.Themaximumindividualisacompositeofthehighestdosefactorofeachagegroup,foreach'rganandtotalbody,andeachnuclide.Sincethecriticalresidencelocationwouldhavethegreatestoccupancytime,theresultantdoseattheresidenceincludingallpathwaysislimiting.However,duetothetechnicalspecif1cationwording,theinhalat1onandgroundplanedoseatthesiteboundaryalongwithallotherpathway's,willbecalculatedassumingacontinuousoccupancytime.tIn11euofcorrectingthelandsiteboundarygroundplaneandinhalationdosefactorsforoccupancyt1me,aTechnicalSpecif1cationchangewillbesubmittedtochangetherequirementfromcalculating"atthesiteboundaryandbeyond"to"atthesiteboundaryorbeyond".Unitlwillthencalculateatthecritical'res1dencesincethisshouldbethe11mit1ngdose.Untilthischangeiseffective,thedoseand/ordoseratecalculationsfortrit1um,iodines,andparticulateswithhalflivesgreaterthan8dayswillconservativelyassumethatthegroundplaneandinhalationpathwaycr1ticalreceptorsareatthesiteboundary,i.e.X/Qand0/Q,respectively,~arecalculatedatthes1teboundary.40 VfIVIC'*
Emergency condenser ventmonitorsetpoints willbeestablished such"thatthereleaserateforradioactive materials ingaseouseffluents donotexceedthe10CFR20limitsforannualreleaserateovertheprojected longestperiodofrelease.Monitorsetpoints fromcontinuous releasepointswillbedetermined onceperquarterundernormalreleaserateconditions andwillbebasedon'the'isotopic composition oftheactualreleaseinprogress, oranoffgasisotopicdistribution oramoreconservative defaultcomposition specified inthepertinent procedure.
3,4RefinementofOffsiteDosesResultingfromEmergencyCondenserVentReleases.Thedosesresultingfrom.theoperationoftheemergencycondensersandcalculatedinaccordancewith3.2.2mayberefinedusingdatafromactualenvironmentalsamples.Grounddepositionsampleswillbeobtainedfromanareaorareasofmaximumprojecteddeposition.Theseareasareanticipatedtobeatornearthesiteboundaryand.nearprojectedplumecenterline.UsingthemethodologyfoundinRegulatoryGuide1.109,thedosewillbecalculatedtothemaximumexposedindividual.Thisdosewillthenbecomparedtothedosecalculatedinaccordancewith3.2.2.Thecomparisonwi11resultin"anadjustmentfactoroflessthanorgreaterthanonewhichwillbeusedtoadjusttheotherdosesfromotherpathways.Otherenvironmentalsamplesmayalsobecollectedandtheresultantcalculateddosestothemaximumexposedindividualcomparedtothedosecalculatedper3.2.2.,Otherenvironmentalsamplemediamay.includemilk,vegetation(suchasgardenbroadleafvegetables),etc.Theadjustmentfactorsfromthesepathwaysmaybeappliedtothedosescalculatedper3.2.2onapathwaybypathwaybasisorseveralpathwayadjustmentfactorsmaybeaveragedandusedtoadjustcalculateddoses.Dosescalculated'fromactualenvironmentalsamplemediawillbebasedonthemethodologypresentedinRegulatoryGuide1.109.Theregulatoryguideequationsmaybeslightlymodifiedtoaccountforshortintervalsoftime(lessthanoneyear)ormodifiedforsimplicitypurposesbydeletingdecayfactors.Deletionofdecayfactorswoul'dyieldmoreconservativeresults.
Ifthecalculated setpointtshigherthantheexistingsetpoint, itisnotmandatory thatthesetpointbechanged.Monitorsetpoints foremergency condenser ventmonitorsareconservatively fixedat5mr/hrforreasonsdescribed inSections3.1.4andtherefore donotrequireperiodicrecalculations.
c~1*III 4.040CFR190REQUIREMENTSThe"UraniumFuelCycle"isdefinedin40CFRPart190.02(b)asfollows:"Uraniumfuelcyclemeanstheoperationsofmillingofuraniumore,chemicalconversionofuranium,isotopicenrichmentofuranium,fabricationofuraniumfuel,generationofelectricitybyalight-water-coolednuclearpowerplantusinguraniumfuel,andreprocessingofspenturaniumfuel,totheextentthatthesedirectlysupporttheproductionofelectricalpowerforpublicuseutilizingnuclearenergy,butexcludesminingoperations,operationsatwastePdisposalsites,transportationofanyradioactivematerialinsupportoftheseoperations,andthereuseofrecoverednon-uraniumspecialnuclearandby-productmaterialsfromthecycle."Section3.6.15.doftheTechnicalSpecificationsrequiresthatwhenthecalculateddosesassociatedwiththeeffluentreleasesexceedtwicethelimitsofsections3.6.15.a.(2)(b),3.6.15.b.(2)(b)and3.6.15.b.(3)(b),thencalculationsshallbemadeincludingdirectradiationcontributionsfromthereactorunitsandoutsidestoragetanks(asapplicable)todeterminewhetherthe40CFR190doselimitshavebeenexceeded.  
Underabnormalsitereleaserateconditions, monitor.alarmsetpoints.
fromcontinuous releasepointswillberecalculated and,ifnecessary, resetatmorefrequentintervals asdeemednecessary by.CORMSupervision.
Inparticular, contributions frombothJAFandNMP-2andtheEmergency Condenser Ventsshallbeassessed:
"Duringoutagesanduntilpower.operation isagainrealized, thelastoperating stackandoffgasmonitoralarmsetpoints shallbeused.
k7i'tZF<~P 3.1.1(Cont'd)Sincemonitorsrespondtonoblegasesonly,monitoralarmpointsaresettoalarmpriortoexceeding thecorresponding totalbodydose'rates.Theskindoseratelimitisnotusedinsetpointcalculations becauseitisneverlimiting.
3.1..2,StackMonitorSetpoints Thedetailedmethodsforestablishing setpoints shallbecontained inthestationprocedures.
Thesemethodsshallapplythefollowing generalcriteria:
(1)Rationale forStackmonitorsettingsisbasedonthegeneralequation:
releaserateactualcorresponding doserate,actualreleaseratemax.allowable corresponding doserate,max.allowable
()max500mrem/yrwhere:Vireleaserateforeachisotopei,uCi/secgamma'hole bodydosefactorinunitsofmrem/yrperuCi/sec(SeeTable3-2)(Q)maxinstantaneous releaseratelimituCi/sec18  
+a'v'1~IIQ%l''tl 3.1.2(Cont'd)(2)Toensurethat10CFR20andTechnical Specifications doseratelimitsarenotexceeded, thehihialarmsonthestackmonitorsshallbesetlowerthanorequalto(0.9)(Q).Hialarmsmax'hallbesetlowerthanorequalto(0.5)(Q)max'3)Basedontheaboveconservatism, thedosecontribution fromJAFandNMP-2canusual,lybeignored..DuringEmergency Classifications atJAForNMP-2duetoairborneeffluent, orafteremergency
.condenser vent;releases
.of-significant proportions, the500mrem/yrvaluemaybereducedaccordingly.
(4)ToconvertmonitorgrosscountratestouCi/secreleaserates,thefollowing generalformulashallbeapp'lied:
(C-B)KQuCi/secreleaseratewhere:'BKsCmmonitorgrosscountrateincpsorcpm;cpscountspersecond,cpmcountsperminutemonitorbackground countratestackmonitorefficiency factorwithunitsofuCi/sec-cps oruCi/sec-cpm (5)MonitorKfactorsshallbedetermined usingthegeneralformula:KQiQi/(C-8)where:individual radionuclide stackeffluent.releaserateasdetermined byisotopicanalysis.
Kfactorsmoreconservative thanthosecalculated bythe-abovemethodology maybeassumed.-19  
,bt'4r~II4U 3.1.2(Cont'd)Alternatively, whenstackreleaseratesarenearthelowerlimitofdetection, thefollowing generalformulamaybeused.tocalculate k:1/KsE~(ii~kYkEk)3.7E4dff'-uCiwhere:fstackflowincc/secEefficiency inunitsofcpm-cc/uCi orcps-cc/uCi (cpmcountsperminute;cpscountspersecond)Ekcpm-cc/bps orcps-cc/psFromenergycalibration curveproducedduringNBStraceable primarygascalibration ortransfersourcecalibration (bpsbetapersecond;psgammaspersecond)Ykb/d(betas/disintegration) orV/d(gammas/d)
FiActivityfractionofnuclideiinthemixtureinuclidecounterk.discreteenergybetaorgammaemitterpernuclidecountersi~secondsThismonitorcalibration methodassumesanoblegasdistribution typicalofarecoilreleasemechanism.
Toensurethatthecalculated efficiency isconservative, betaorgammaemissions whoseenergyisabovetherangeofcalibration ofthedetectorarenotincludedinthecalculation.
Q}4 3.1.3Recomb)ner Discharge
<DffGas)MonitorSetpoints (1)Thehihialarmpointsshallactivatewithrecombiner discharge ratesequaltoorlessthan500,000uCi/sec.Thisalarmpointmaybesetequal-.to orlessthan1Ci/secforaperiodoftimeInottoexceed60daysprovidedtheoffgastreatment systemisinoperation.
(2)Thehialarmpointsshallactivatewithrecombiner discharge ratesequaltoorlessthan500,000uCi/sec(3)ToconvertmonitormR/hrreadingstouCi/sec,theformulabelowshallbeapplied:<R)(KR)QRuCi/secrecombiner discharge releaserate"where:RmR/hrmonitorindicator KRefficiency factorinunitsofuCi/sec/mR/hr determined priortosettingmonitoralarmpoints(4)MonitorKRfactorsshallbedetermined usingthegeneralformula:KRQi/Rwhere:Qi-individual radionuclide recombiner discharge releaserateasdetermined byisotopicanalysisandflowratemonitor.KRfactorsmoreconservative thanthosecalculated bytheabovemethodology maybeassumed.
J4jCIf4/Qi'lag'I~ppAl 3.1.3(Cont'd)(5)Thesetpoints chosenprovideassurance thatthetotalbodyexposuretoanindividual attheexclusion areaboundarywillnotexceedaverysmallfractionofthelimitsof10CFRPart100intheeventthiseffluentisinadvertently discharged directlytotheenvironment withouttreatment (therebyimplementing therequirements ofGeneralOesignCriteria60and64ofAppendixAto10CFRPart,50)..Additionally, thesesetpoints serveto,limitbuildupoffissionproductactivitywithinthestation.systemswhichwouldresultifhighfuelleakageweretobepermitted overextendedperiods.3.1.4Emergency Condenser VentHonitorSetpointThemonitorsetpointwasestablished bycalculation
("Emergency
,Condenser VentHonitorAlarmSetpoint",
January13,1986,NHPCFileCode&#xb9;'l61*99).
Assumingahypothetical casewith(1)reactorwatertiodineconcentrations higherthantheTechnical Specification Limit,(2)reactorwaternoblegasconcentrations higherthanwouldbeexpectedatTechnical Specification iodinelevels,and(3)leakageofreactorsteamintotheemergency condenser shellat300'Aofratedflow(or1.3E6lbs/hr),thecalculation predictsanemergency condenser ventmonitorresponseof20mR/hr.Suchareleasewouldresultinlessthan'0CFR20.doseratevaluesatthesiteboundaryandbeyondfortypical"emergency condenser cooldownperiods.Sincea20mR/hrmon'itorresponsecan,intheory,beachievable onlywhenreactorwateriodinesarehigherthanpermitted byTechnical Specifications, aconservative monitorsetpointof5mr/hrhasbeen-adopted.
IICof~hVWII,aITWIr'Tr~'t.ITl\ITttI0 3.1.5Discussion 3.1.5.1StackEffluentMonitoringSystemDescription
-TheNMP-1Stack'EffluentaMonitoring Systemconsistsoftwosubsystems; theRadioactive GaseousEffluentMonitoring System(RAGEMS)andtheoldGeneralElectricStackMonitoring System(OGESMS).
Duringnormaloperation, theOGESMSshallbeusedtomonitorstationnoble'aseffluents andcollectparticulates andiodinesamplesincompliance withTechnical Specification requirements.
TheRAGEMS.is designedtobepromptlyactivated fromtheMainControl"Roomforuseinhighrangemonitoring duringaccidentsituations incompliance withNUREG0737criteria.
Overallsystemschematic fortheOGESMSandRAGEMSareshownonFigureB-9.Asimplified viewofRAGEMSShowingUnit0,1,2,3and4canbefoundonFigureB-S.TheRAGEMScanprovidecontinuous accidentmonitoring andon-lineisotopicanalysisofNMP-1stackeffluentnoblegasesatLowerLevelsofDetection lessthanTechnical Specification Table4.6.15-2limits.Activities aslowas5.0E-Bandashighas2.0E5uCi/ccfornoblegasesaredetectable bythesystem.
i&jan"JP~.0-y~yII~*'Iletgledbl4II 3T.5.2StackSampleflowPath-RAGEHS'"Theeffluentsampleisobtainedinsidethestackatelevation 530'singanisokinetic probewithfourorifices.
Thesamplelinethenbendsradiallyoutandbackintothestack;descendsdownthestackandoutofthestack-atapproximately elevation 257';runshorizontally (enclosed inheattracing)some270'longtheoffgas.tunnel;andenterstheRAGEHSlocatedontheTurbineBuilding250'Dilution cabinet-Unit0)andOffGasBuilding247'Particulate, Iodine,NobleGasstations-Units1-3).'Inthe'Dilution cabinet'of theRAGEHS,thestackgasmaybedilutedduringaccidentsituations approximately 100-200X(firststage)or10000-40000 X(firstandsecondstage)withgaseousnitrogensuppliedfromanon-siteliquidnitrogenstoragetank(seeFigure8-9).FromUnit0,thesamplegasentersUnit1-3ofRAGEHSandflowsthruin-lineparticulate andiodinecartridges andthenthrueithera6liter(lowrange)or30cc(highrange)noblegaschamber.ThesamplegasnextflowsbackthruUnit0andtheoffgastunnel;andbackintothestack.
I1+4gVL41wpfTJ'1SktI' 3.1.5.3StackSampleFlowPath-OGESHSTheOGESHSsampleisobtainedfromthesamestacksampleprobeastheRAGEHS.Fromtheexitofthestackatelevation 257',thesamplelinerunseastapproximately 20'ndthenvertically approximately 8'otheOGESMSskid.IntheOGESMS,sampleflowsthruaparticuate/,
.iodinecartridge housingand.fournoblegasscintillation detectors (i.e..07and08lowrange-beta detectors andRN-03AandRN-038highrangegammadetectors).
FromOGESHS,thestacksampleflowsbackintothestackatapproximately elevation 257'.AllOGESMSdetectoroutputsaremonitored andrecordedremotelyintheHainControlRoom.Alarmingcapabilities areprovidedtoalertOperators ofhighreleaserateconditions priortoexceeding Technical Specification 3.6.15.b(1)adoseratelimits.,Stackparticulate andiodinesamplesareretrieved manuallyfromtheOGESMSandanalyzedinthelaboratory usinggammaspectroscopy atfrequencies andLLOsspecified inTable4.6.15-2oftheTechnical Specifications.
I'tI*P'tF 3.1.5.4SamplingFrequency/Sample AnalysisRegardless ofwhichstackmonitoring subsystem isutilized, radioactive gaseous"wastes
.shallbesampledandanalyzedinaccordance withthesamplingandanalysisprogramspecified inTechnical Specification Table4.6.15-2.
Particulate samplesaresavedandanalyzedforprincipal gammaemitters, grossalpha,Fe-55,Sr-89,Sr-90atmonthlyintervals minimally.
Thelatterthreeanalysesareperformed off-sitefromacomposite sample.Sampleanalysisfrequencies areincreased duringelevatedreleaserateconditions, following startup,shutdownandinconjunction witheachdrywellpurge.Consistent withTechnical Specification Table4.6.15-2, stackeffluenttritiumissampledmonthly,duringeachdrywellpurge,and.weeklywhenfuelisoffloadeduntilstablereleaseratesaredemonstrated.
Samplesareanalyzedoff-site.
Linelosscorrection factorsareappliedtoallparticulate and"*"i,iodine.results.-Correction factorsof2.0and1.5areusedfordataobtainedfromRAGEHSandOGESHSrespectively.
Thesecorrection factorsarebasedonempirical datafromsamplingconducted atNHP-1in1985(memofromJ.BlasiaktoRAGEHSFile,1/6/86,"StackSampleRepresentativeness Study:RAGEHSvs.In-StackAuxiliary ProbeSamples").  
~k(1I~'i 3.1.5.5I-133Estimates Monthly,thestackeffluentshallbesampledforiodinesovera24hourperiod-andtheI-135/I-131,and theI-133/I-131 ratioscalculated.
Theseratiosshallbeusedtocalculate I-133,I-135releaseforlongeracquisition samplescollected duringthemonth.Additionally, theI-135/I-131 andI-133/I-131 ratiosshouldalsobedetermined afterasignificant change-intheratioissuspected (eg,plantstatuschangesfromprolonged shutdowntopoweroperation orfueldamagehasoccurred).
3.1.5.6GaseousRadwasteTreatment SystemOperation Technical Specification 3.6.16.brequiresthatthegaseousradwastetreatment systemshallbeoperableandshallbeusedtoreduceradioactive materials ingaseouswastepriortotheirdischarge asnecessary tomeettherequirements ofTechnical Specification 3.6.15.b.
ToensureTechnical Specification 3.6.15.blimitsarenotexceeded, andtoconfirmproperradwastetreatment systemoperation asapplicable, cumulative dosecontributions forthecurrentcalendarquarterandcurrentcalendaryearshallbedetermined monthlyinaccordance withsection3.2ofthismanual.Initialdosecalculations shallincorporate.
thefollowing-assumptions with,regardtoreleaseratesofnon-gamma emittingradionuclides subsequently analyzedoff-site:  
$l4gP">>'"wh'w'N~y'~~
~'oi"pt, 3.1.5.6(Cont'd)a)H-3releaserate24uCi/secb)Sr-89releaserateZ4xCs-137releaseratec)Sr-90releaserateZ0.5xCs-137releaserated)Fe-55releaserate21xCo-60releaserateAssumedreleaseratesrepresent conservative estimates derivedfromanalysisofhistorical datafromeffluentreleasesandprocesswastestreams(SeeNAP34023,C.HaretoJ.Blasiak,April29,1988,"DoseEstimates forBeta-Emitting Isotopes"
).Following receiptofoff-siteH-3,Sr-89,Sr-90,,Fe-55 analysisinformation, doseestimates shallberevisedusingactualradionuclide concentrations.
3.2DoseandDoseRateDeterminations Inaccordance withspecifications 4.6.15.b.
(1),4.6.15.b.
(2),and4.6.15.b.(3) doseanddoseratedeterminations willbemademonthlytodetermine:
(1)TotalbodydoseratesandgammaairdosesatthemaximumX/Q'landsectorsiteboundaryinterface andbeyond.(2)Skindoseratesandbetaairdosesatthe.maximumX/Qlandsectorsite'boundary interface andbeyond.(3)ThecriticalorgandoseanddoserateatthemaximumX/Qlandsectorsiteboundaryinterface andatacriticalreceptorlocationbeyondthesiteboundary..
28  
'pEv 3.2(Cont'd)Averagemeteorological data(ie,maximumfiveyearannualaverageX/QandD/Qvaluesinthecaseofelevatedreleasesor1985annualaverageX/QandD/Qvalues,inthecaseofgroundlevelreleases) shallbeutilizedfordoseanddoseratecalculations.
Whereaveragemeteorological dataisassumed,doseanddoseratesduetonoblegasesatlocations beyondthesiteboundarywillbelowerthanequivalent siteboundarydose-anddoserates.Therefore, undertheseconditions, calculations ofnoblegasdoseanddoseratesbeyondthemaximumX/Qlandsectorsiteboundarylocations canbeneglected.
Thefrequency ofdoseratecalculations willbeupgradedwhenelevatedreleaserateconditions specified insubsequent sections3.2.1.1and3.2.1.2arerealized.
rEmergency condenser ventreleasecontributions tothemonthlydoseanddoseratedeterminations willbeconsidered onlywhentheemergency condenser returnisolation valveshavebeenopenedforreactorcooldownorifEmergency Condenser tubeleaksdevelopwithorwithoutthesystem'sreturnisolation valveopened.Withouttubeleakageoropeningofthereturnisolation valves,releasesfromthissystemarenegligible andthecorresponding dosecontributions donothavetobeincluded.
I I*me'q<a<~"<~,q"".'ltFgv, 3.2(Cont'd)Hhenreleasesfromtheemergency condenser haveoccurred, doserateanddosedeterminations shall'beperformed usingmethodology in3.2.1and3.2.2.Furthermore, environmental samplingmayalsobeinitiated torefineanyactualcontribution todoses.SeeSection3.4.Criticalorgandoses.anddoseratesmaybeconservatively calculated..
byassuming.theexistence ofamaximumindividual.
Thisindividual isacomposite ofthehighestdosefactorofeachagegroup,foreachorganandtotalbody,andeachnuclide.Itisassumedthatallpathwaysareapplicable andthehighestX/Qand/or0/QvalueforactualpathwaysasnotedinTable3-1areineffect.Themaximumindividual's doseisequaltothesamedosethatpersonwouldreceiveiftheyweresimultaneously sub]ected tothehighestpathwaydoseateachcriticalreceptoridentified foreachpathway.Thepathwaysincludegrass-(cow andgoat)-milk, grass-cow-meat, vegetation, groundplaneandinhalation.
TocomplywithTechnical Specifications wewillcalculate themaximumindividual doserateatthesiteboundaryand"'eyondatthecriticalresidence.
Ifdoseordoseratescalculated, usingtheassumptions notedabove,reachTechnical Specification limits,actualpathwayswillbeevaluated, anddose/dose ratesshallbecalculated atseparatecriticalreceptorlocations andcomparedwithapplicable limits.30 ekedAI6'ltIII, 3.2.1DoseRate'ose'rateswillbe-calculated.
monthly,ataminimum,orwhentheHi-Histackmonitoralarmsetpointisreached,todemonstrate thatdoseratesresulting fromthereleaseofnoblegases,tritium,iodines,andparticultes withhalflivesgreaterthan8daysare'ithinthelimitsspecified inlOCFR.20.
Theselimitsare:NobleGasesHholeBodyDoseRate500mrem/yrSkinDoseRate3000mrem/yrTritiumIodinesandParticulates OrganDoseRate1500mrem/yr3.2.1.1NobleGasesThefollowing noblegasdoserateequationincludesthecontribution fromthestack(s)elevatedreleaseandtheemergency condenser vent(v)groundlevelreleasewhenapplicable (See.section3.2).31 Pf~
fortotalbodydoserates(mrem/sec):
ORg(mrem/sec)
-3.17E-8Zi.[ViQi,+Ki(X/Q)Qi]i''iis'vivForskindoserates(mrem/sec):
OR~+8(mrem/sec)-
3.17E-8Zi[(Li(X/Q)s+1.118i)Qis+(Li+1.11Ni)<X/Q)vQiv~
where:OR~totalbodygammadoserate(mrem/sec).
OR~+6skindoseratefromgammaandbetaradiation (mrem/sec).
=='he.constant, accounting forthegammawholebodydoseratefromstackradiation, foranelevatedfiniteplumereleasesforeachidentified noblegasnuclide,i.ListedonTable3-2inmrem/yrperuCi/sec..
Kitheconstantaccounting forthegammawholebodydoseratefromimmersion inthesemi-infinite cloudforeachidentified noblegasnuclide,i.ListedinTable3-3inmrem/yrperuCi/m3(fromReg.Guide1.109)Qithereleaseofisotopei;(uCi;sstack,vvent).X/Q-therelativeplumeconcentration
<inunitsofsec/m3)atthelandsectorsiteboundaryorbeyond.'Averagemeteorological data(Table3-1)isused.'"Elevated" X/Qvaluesareusedforstackreleases(s",'stack);
"Ground"X/QvaluesareusedforEmergency Condenser Ventreleases(vvent).theconstantaccounting forthebetaskindoseratefromimmersion inthesemi-infinite cloudforeachidentified noblegasnuclide,i.ListedinTable3-3:inmrem/yrperuCi/m3(fromReg.Guide1.109),.theconstant.accounting for,the'airgammaradiation fromtheelevatedFiniteplumeresulting fromstackreleasesforeachidentified noblegasnuclide,i.ListedinTable3-2inmrad/yrperuCi/sec.Hitheconstantaccounting forthegammaairdoseratefrom-immersion inthesemi-infinite cloudforeachidentified noblegasnuclide,i.ListedinTable3-3inmrem/yrperuCi/m3(fromReg.Guide1.109)SeeAppendix8forderivation ofBi,andVi.32 srfP.Ag<
3.2.1.2Tritium,lodinesandParticulates Toensurethatthe'500'mrem/year sitedoseratelimitisnotexceeded, offsitedoseratesfortritium,iodineandparticulates withhalflivesgreaterthan8daysshallbecalculated monthlyandwhenreleaserates(Q).exceed0.34uCi/secusingthefollowing equation.
Oak(mrem/sec) 3.17E-8$~(~iRijak[Wsis+WvivWhere:oakTotaldosetoeachorgankofanindividual inagegroupa(mrem/sec).
dispersion parameter eitherX/Q(sec/m3)or0/Q(1/m2)depending onpathwayandreceptorlocationassumed.Averagemeteorological datais"used(Table3-1)."Elevated" W~valuesareusedforstackreleases(sstack);"Ground"WgvaluesareusedforEmergency Condenser Ventreleases(vvent).QiRi]ak3.17E-.Sthetotalquantityofisotopeireleased, (uCi/sec; sstack,vvent)thedosefactorforeachisotopei,pathway],agegroupa,andorgank(Table3-4,through3-22;m2-mrem/yr peruCi/secforallpathwaysexceptinhalation, mrem/yrperuCl/m3.theinverseofthenumberofsecondsinayear.,TheR.valuescontained inTables3-4through3-22.werecalculated usingthemethodology definedinNUREG-0133 andparameters fromRegulatory Guide1.109,Revision1;aspresented inAppendixC.When-thereleaserateexceeds0.34uCi/sec,thedoserateassessment shallalsoincludeJAFandNMP-2contribution.
33 Pp4SA+v,1<
Theuseofthe0.34uCi/secreleaseratethreshold toperformdoseratecalculations isjustified asfollows:(a)The1500mrem/yrorgandoseratelimitcorresponds toaminimumreleaseratelimitof0.34uCi/seccalculated usingtheequation:
1500(Q/sec)x(Ri)N))where:1500siteboundarydoseratelimit(mrem/year)
(Ri]"])max themaximumcurie-to-dose conversion factorequalto4.45E3mrem-sec/uCi-yr forSr-90,childboneatthecriticalresidence receptorlocationbeyondthesiteboundary.
(b)Theuseof0.34uCi/secreleaseratethreshold andthe4.45E3mrem-sec/uCi-yr curie-to-dose conversion factorisconservative sincecurie-to-dose conversion factorsforotherisotopeslikelytobepresentaresignificantly lower.
bfIs'4 3.2.2Dose-Calculations willbeperformed.
monthlyataminimum,.todemonstrate thatdosesresulting fromthereleaseofnoblegases,tritium,iodines,andparticulates withhalflivesgreaterthan8daysarewithinthelimitsspecified in10CFR50,AppendixI.Theselimitsare:NobleGases5mRgamma/calendar quarter'0mradbeta/calendar quarter10mRgamma/calendar year'0mradbeta/calendar yearTritiumIodinesandParticulates 7.5mremtoanyorgan/calendar quarter15mremtoanyorgan/calendar year l+%i'Id4II'PtI1' 3.2.2.1NobleGasAirDoseThefollowing NobleGasairdoseequationincludescontributions fromthestack(s)elevated.release.and theemergency condenser vent(v)groundlevelreleasewhenapplicable (seesection3.2):Forgammaradiation.
(mrad):Dg(mrd)317E8~iHi(XQ)vQiv+BiQisForbetaradiation (mrad):08(mrad)3.17E-SX)Ni(XQ)viv+siswhere:0ygammaairdose(mrad)0>betaairdose(mrad)theconstantaccounting fortheairgammaradiation fromtheelevatedfiniteplumeresulting fromstackreleasesforeachidentified noblegasnuclide,i.ListedinTable3-2inmrad/yr,peruCi/sec.NiTheconstantaccounting fortheairbetadosefromimmersion inthesemi-infinite cloudforeachidentified noblegasnuclide,i.ListedonTable3-3inmrad/yrperuCi/m3(fromReg.Guide1.109).Qithetotalquantityofisotopeireleased, (uCi/sec.)
NotethattheunitsforthegammaairdoseareinmradcomparedtotheunitsforthelimitsareinmR.TheNRCrecognizes that1mR1mrad,forgammaradi'ation.
36 4q(gi 3.17E-Stheinverseofthenumberofsecondsinayear.theconstantaccounting fortheairgammadosefromimmersion inthesemi-infini tecloudforeachidentified noblegasnuclide,i.ListedonTable3-3inmrad/yrperuCi/m3<fromReg.Guide1.109).Allotherparameters areasdefinedinsection3.2.1.1.3.2.2.2Tritium,IodinesandParticulates
'oensurethatthe15mrem/yrfacilitydoselimitisnotexceeded, offsitedosesfortritium,iodines,andparticulates withhalflivesgreaterthan8daysshallbecalculated monthlyusingthefollowing
.<<equation:
0ak(mrem)3.17E-8Z~(SiRi]akWsis+WvivWhere:0akWgQiRi~ak3.17E-8Totaldosetoeachorgankofanindividual inagegroupa(mrem).dispersion parameter eitherX/Q(sec/m3)or0/Q(1/m2)depending onpathwayandreceptorlocationassumed.Averagemeteorological dataisused(Table3-1)."Elevated" W~valuesareused.forstackreleases(sstack);"Ground"W~valuesareusedforEmergency Condenser Ventreleases(vvent).thetotalquantityofisotopeireleased,
<uCi/sec; s-stack,vvent)thedosefactorforeachisotopei,pathway],agegroupa,andorgank(Tables3-4,through3-22;m2-mrem/yr peruCi/sec)'theinverseofthenumberofsecondsinayear37 fII~0hlyCE' TheRvaluescontained inTables3-4through3-22werecalculated usingthemethodology definedinNUREG-0133 andparameters fromRegulatory Guide1.109,Revision1;aspresented inAppendixC.3.2.2.3Accumulating DosesDoseswillbecalculated monthly,ataminimum,forgammaair,betaair,andthecriticalorganforeachagegroup.Doseestimates will,also,becalculated monthlypriortoreceiptofanyoffsiteanalysisdatai.e.,strontium, tritium,andiron-55.Resultswillbesummedforeachcalendarquarterandyear.Thecriticaldosesarebasedonthefollowing:
noblegasplumeairdosedirectradiation fromgroundplanedeposition inhalation dosecowmilkingestion dosegoatmilkingestion dose'cowmeatingestion dosevegetation (foodcrops)ingestion doseThequarterly andannualresultsshallbecomparedtothelimitslistedinparagraph,3.2.2.
If,thelimitsareexceeded, specialreports,asrequiredbySection6.9.3oftheTechnical-Specification, shallbesubmitted.
38 A~"I 3.3CriticalReceptors Inaccordance withtheprovisions of10CFR20and10CFR50,AppendixI,thecriticalreceptors havebeenidentified andare"contained inTable3-1.Forelevatednoblegasreleasesthecriticalreceptoristhesiteboundary.
Hhen1985averageannualX/Qvaluesareusedforgroundlevelnoblegasreleases, thecriticalreceptoristhemaximumX/Qlandsectorsiteboundaryinterface.
Fortritium,iodines,andparticulates withhalflivesgreaterthaneightdays,thecriticalpathwaysaregrass-(cow andgoat)-milk, grass-cow meat,vegetation, inhalation anddirectradiation (groundplane)asaresultofgrounddeposition.
Thegrass-(cow andgoat)-milk, andgrass-cow-meat pathwayswillbebasedonthegreatest0/Qlocation.
Thislocationhasbeendetermined incon]unction withthelandusecensus(technical specification 3.6.22)andissub]ecttochange.Thevegetation (foodcrop)pathwayisbasedonthegreatest0/Qgardenlocationfromwhich,samplesaretaken.Thislocationmayalsobemodifiedasaresultof-vegetation samplingsurveys.39  
$*PC4gi+1 3.3(Cont'd)TocomplywithTechnical Specifications, theinhalation andground'lanedosepathwayswill.be.,calculated atthesiteboundaryandbeyondatthecriticalresidence.
BecausetheTechnical Specifications statetocalculate "atthesiteboundaryandbeyond",insteadof"atthesiteboundaryorbeyond",suchasUnit2,thedosesand/ordoseratesmustbecalculated foramaximumindividual whoisexposedtoallpathwaysatthesiteboundaryandatthecriticalresidence.
Themaximumindividual isacomposite ofthehighestdosefactorofeachagegroup,foreach'rganandtotalbody,andeachnuclide.Sincethecriticalresidence locationwouldhavethegreatestoccupancy time,theresultant doseattheresidence including allpathwaysislimiting.
However,duetothetechnical specif1cation wording,theinhalat1on andgroundplanedoseatthesiteboundaryalongwithallotherpathway's, willbecalculated assumingacontinuous occupancy time.tIn11euofcorrecting thelandsiteboundarygroundplaneandinhalation dosefactorsforoccupancy t1me,aTechnical Specif1cation changewillbesubmitted tochangetherequirement fromcalculating "atthesiteboundaryandbeyond"to"atthesiteboundaryorbeyond".Unitlwillthencalculate atthecritical'res1dence sincethisshouldbethe11mit1ngdose.Untilthischangeiseffective, thedoseand/ordoseratecalculations fortrit1um,iodines,andparticulates withhalflivesgreaterthan8dayswillconservatively assumethatthegroundplaneandinhalation pathwaycr1ticalreceptors areatthesiteboundary, i.e.X/Qand0/Q,respectively,
~arecalculated atthes1teboundary.
40 VfIVIC'*
3,4Refinement ofOffsiteDosesResulting fromEmergency Condenser VentReleases.
Thedosesresulting from.theoperation oftheemergency condensers andcalculated inaccordance with3.2.2mayberefinedusingdatafromactualenvironmental samples.Grounddeposition sampleswillbeobtainedfromanareaorareasofmaximumprojected deposition.
Theseareasareanticipated tobeatornearthesiteboundaryand.nearprojected plumecenterline.
Usingthemethodology foundinRegulatory Guide1.109,thedosewillbecalculated tothemaximumexposedindividual.
Thisdosewillthenbecomparedtothedosecalculated inaccordance with3.2.2.Thecomparison wi11resultin"anadjustment factoroflessthanorgreaterthanonewhichwillbeusedtoadjusttheotherdosesfromotherpathways.
Otherenvironmental samplesmayalsobecollected andtheresultant calculated dosestothemaximumexposedindividual comparedtothedosecalculated per3.2.2.,Otherenvironmental samplemediamay.includemilk,vegetation (suchasgardenbroadleaf vegetables),
etc.Theadjustment factorsfromthesepathwaysmaybeappliedtothedosescalculated per3.2.2onapathwaybypathwaybasisorseveralpathwayadjustment factorsmaybeaveragedandusedtoadjustcalculated doses.Dosescalculated'from actualenvironmental samplemediawillbebasedonthemethodology presented inRegulatory Guide1.109.Theregulatory guideequations maybeslightlymodifiedtoaccountforshortintervals oftime(lessthanoneyear)ormodifiedforsimplicity purposesbydeletingdecayfactors.Deletionofdecayfactorswoul'dyieldmoreconservative results.
c~1*III  
 
==4.0 40CFR190REQUIREMENTS==
The"UraniumFuelCycle"isdefinedin40CFRPart190.02(b)asfollows:"Uraniumfuelcyclemeanstheoperations ofmillingofuraniumore,chemicalconversion ofuranium,isotopicenrichment ofuranium,fabrication ofuraniumfuel,generation ofelectricity byalight-water-cooled nuclearpowerplantusinguraniumfuel,andreprocessing ofspenturaniumfuel,totheextentthatthesedirectlysupporttheproduction ofelectrical powerforpublicuseutilizing nuclearenergy,butexcludesminingoperations, operations atwastePdisposalsites,transportation ofanyradioactive materialinsupportoftheseoperations, andthereuseofrecovered non-uranium specialnuclearandby-product materials fromthecycle."Section3.6.15.doftheTechnical Specifications requiresthatwhenthecalculated dosesassociated withtheeffluentreleasesexceedtwicethelimitsofsections3.6.15.a.(2)(b),
3.6.15.b.(2)(b) and3.6.15.b.(3)(b),
thencalculations shallbemadeincluding directradiation contributions fromthereactorunitsandoutsidestoragetanks(asapplicable) todetermine whetherthe40CFR190doselimitshavebeenexceeded.  
$1%
$1%
4.0(Cont'd)Ifsuchisthecase,NiagaraMohawkshallsubmitaSpecialReporttoth'e'NRCandlimit"subsequentreleasessuchthatthedosecommitmenttoarealindividualfromalluraniumfuelcyclesourcesislimitedto<25mremtothetotalbodyoranyorgan(exceptthethyroid,whichislimitedto<75mrem)overthecalendaryear.Thisreport=istodemonstratethat.radiationexposurestoallrealindividualsfromalluraniumfuelcyclesources(includingallliquidandgaseouseffluentpathwaysanddirectradiation)arelessthanthelimitsin40CFRPart190.Ifreleasesthatresultindosesexceedingthe40CFR190limitshaveoccurred,thenavariancefromtheNRCtopermitsuchreleaseswillberequestedandifpossible,actionwillbetakentoreducesubsequentreleases.ThereporttotheNRCshallcontain:1)'dentificationof,alluraniumfuelcyclefacilitiesoroperationswithin5milesofthenuclearpowerreactorunitsat.thesitethatcontributetotheannualdoseofthemaximumexposedmemberofthepublic.2)Identificationofthemaximumexposedmemberof-thepublicandadeterminationofthetotalannualdosetothispersonfromexistingpathwaysandsourcesofradioactiveeffluentsanddirectradiation.  
4.0(Cont'd)Ifsuchisthecase,NiagaraMohawkshallsubmitaSpecialReporttoth'e'NRCandlimit"subsequent releasessuchthatthedosecommitment toarealindividual fromalluraniumfuelcyclesourcesislimitedto<25mremtothetotalbodyoranyorgan(exceptthethyroid,whichislimitedto<75mrem)overthecalendaryear.Thisreport=istodemonstrate that.radiation exposures toallrealindividuals fromalluraniumfuelcyclesources(including allliquidandgaseouseffluentpathwaysanddirectradiation) arelessthanthelimitsin40CFRPart190.Ifreleasesthatresultindosesexceeding the40CFR190limitshaveoccurred, thenavariancefromtheNRCtopermitsuchreleaseswillberequested andifpossible, actionwillbetakentoreducesubsequent releases.
ThereporttotheNRCshallcontain:1)'dentification of,alluraniumfuelcyclefacilities oroperations within5milesofthenuclearpowerreactorunitsat.thesitethatcontribute totheannualdoseofthemaximumexposedmemberofthepublic.2)Identification ofthemaximumexposedmemberof-thepublicandadetermination ofthetotalannualdosetothispersonfromexistingpathwaysandsourcesofradioactive effluents anddirectradiation.  
~-
~-
4.p(Cont'd)Themaximumtotalbodyandorgandosesresultingfromradioactivematerialinliquideffluents"fromNineHilePointUnit1willbesummedwiththemaximumdosesresultingfromthereleasesofnoblegases,radioiodines,andparticulatesfortheothercalendarquarters(asapplicable)andfromthecalendarquarterinwhichtwicethe'
4.p(Cont'd)Themaximumtotalbodyandorgandosesresulting fromradioactive materialinliquideffluents"from NineHilePointUnit1willbesummedwiththemaximumdosesresulting fromthereleasesofnoblegases,radioiodines, andparticulates fortheothercalendarquarters(asapplicable) andfromthecalendarquarterinwhichtwicethe'imitwasexceeded.
Thedirectdosecomponents willbe-determined byeithercalculation oractualmeasurement.
Actualmeasurements willutilizeenvironmental TLOdosimetry.
Calculated measurements willUtilizeengineering calculations todetermine aprojected directdosecomponent.
Intheeventcalculations areused,themethodology will"bedetailedasrequiredinSection6.9.3.eoftheTechnical Specifications.
ThedosesfromNineHilePointUnit1willbeaddedtothedosestothemaximumexposedindividual thatarecontributed fromotheruraniumfuelcycleoperations within5milesofthesite.Forthepurposeofcalculating doses,theresultsoftheRadiological Enviromental Honitoring Programmaybeincludedforproviding morerefinedestimates ofdosestoarealmaximumexposedindividual.
Estimated doses,ascalculated fromstationeffluents, maybereplacedbydosescalculated fromactualenviromental sampleresults..
44 p~if''1E)It\I,*%lPCq Evaluation


NUCLIOEBONELIVERTABLE3-10RiVALUES-CONMILK-CHILDm~mremlr2uCi/secT.BODYTHYROIDKIDNEYLUNGGI-LLI*H3-2.
NUCLIOEBONELIVERTABLE3-10RiVALUES-CONMILK-CHILDm~mremlr2uCi/secT.BODYTHYROIDKIDNEYLUNGGI-LLI*H3-2.05E32.05E32.05E32.05E32.05E32.05E3*C141.65E63.29E53.29E53.29f53.29E53.29E53.29E5Cr515-29E42.93E48.02E35.36E42.&OE6Mn54-1.35E73.59E6Fe557.43E73.94E71.22E7Fe596.55E71.06EB5.28E7Co58-6.96E62.13E73.78E6Co602.89E78.52E7Zn652.63E97'OE94.35E94.41E9Sr893.70E9SI907.53E101.06EB1.91E10Zr952.18E34.&OE24.27E2**Nb951.6&E56.55E44.68E4Mo994.
~5'>>I)~~I)I8)l~~.,Og~~~ill''~IC~)II~.IIII0~tQ~0~~0  
~5'>>I)~~I)I8)l~~.,Og~~~ill''~IC~)II~.IIII0~tQ~0~~0  
&Ew'4Iilla~otalCV'IIO ISOKINETICPROBERN2111241RAGEMSRAGEMSDitutionReturn112-52112-131]SampleReturnDrain112-5511243112-132112.57OGESMSIntet112.30112-56112-133OGESMSOuttetFigureD-9StackSampleandSampleReturnNIAGARAMOHAWKPOWERCORPORATIONNINEMILEPOINT-UNIT1OFFSlTEDOSECALC.MANUAL126-SlitF'~~Jtel RAGEMSinletOVS112-173OV3112-169OV2112-167PCV112-106112-110NeSupplyOV8112-17812-1Pl112-21OV4112-171OFS1112-101AC112.130112-51OV1OV13112-165t1248RAGEMSDilutionInletOFC4112-104OFS4112-04APCV112-107OFC1112-101112-111Pl11-122OFC3112-103OFS3112-103A112-116OCF2112-102OFS2112-102A112-151OV16112-150112-112Pl"11-23OV12Senlpte112+7ReturnRAGEMSOutlet112-113Pl112-24112-117112-118OP2OP1OV6112-175Figure0-1011-44RAGEMSDilutionSchematicNIAGARAMOHAWKPOWERCORPORATIONNINEMlLEPOINT-UNIT1OFFSITEDOSECALC.MANUAL127 IP'~)~ir14glg 112-1141FS1112-129Pl112-1251V31V4112-183112-185,'V32V4112-199112-2013V3112.73V16112-2183V112-96Qalhn2Tritium112-73112-72112-743FS1112-105A1V1112-11V212-'I812VI112-1952112-1973VI3VS112332.776Uter-95112-99.75Pl112-1263GVI112-1051V5112-1861V62VS112-187112-2022V6112-2032V11112-2081176I-78333V4112.98112-1193V63V7112-100112-211Pl112471V11112-192Pl112441V17112493V11112-2153VI112-217'l12-1083PI3VIO112-21I3VI2112-109112-216FiUreD-11RAGEMSSchematicNIAGARAMOHAWKPOWERCORPORATIONNINEMILEPOINT-UNIT1OFFSITEDOSECALC.MANUAL128 P+A.JatAt'a'~<<a1 011242FS1143112-1011249AM43A6711266112-11Inlet112-146112-147112-59FL1112-58112-14812-1491126111240u112-137112-152Pl112-uu1126263112-153BA-G-3112-154'l124411245uu112-1611124811244FGV112-91112-137112-163112-134BRG-3PS2114i11-1351'l2-135112-139112-138112-140FS112-94Fl11246TritiumV/Pl1124512-158q112-156112-155112-142l12-141112-22FL3112-20112.2111240112-159112-'157112-3112-19112-112112.14112.1811249112-70112-1512-1112-121124711248FiureD-12OGESMSSchematicNIAGARAMOHAWKPOWERCORPORATIONNINEMILEPOINT-UNIT1OFFSITEDOSECALC.MANUAL129-  
&Ew'4Iilla~otalCV'IIO ISOKINETIC PROBERN2111241RAGEMSRAGEMSDitutionReturn112-52112-131]SampleReturnDrain112-5511243112-132112.57OGESMSIntet112.30112-56112-133OGESMSOuttetFigureD-9StackSampleandSampleReturnNIAGARAMOHAWKPOWERCORPORATION NINEMILEPOINT-UNIT1OFFSlTEDOSECALC.MANUAL126-SlitF'~~Jtel RAGEMSinletOVS112-173OV3112-169OV2112-167PCV112-106112-110NeSupplyOV8112-17812-1Pl112-21OV4112-171OFS1112-101AC112.130112-51OV1OV13112-165t1248RAGEMSDilutionInletOFC4112-104OFS4112-04APCV112-107OFC1112-101112-111Pl11-122OFC3112-103OFS3112-103A112-116OCF2112-102OFS2112-102A112-151OV16112-150112-112Pl"11-23OV12Senlpte112+7ReturnRAGEMSOutlet112-113Pl112-24112-117112-118OP2OP1OV6112-175Figure0-1011-44RAGEMSDilutionSchematic NIAGARAMOHAWKPOWERCORPORATION NINEMlLEPOINT-UNIT1OFFSITEDOSECALC.MANUAL127 IP'~)~ir14glg 112-1141FS1112-129Pl112-1251V31V4112-183112-185,'V3 2V4112-199112-2013V3112.73V16112-2183V112-96Qalhn2Tritium112-73112-72112-743FS1112-105A1V1112-11V212-'I812VI112-1952112-1973VI3VS112332.776Uter-95112-99.75Pl112-1263GVI112-1051V5112-1861V62VS112-187112-2022V6112-2032V11112-2081176I-78333V4112.98112-1193V63V7112-100112-211Pl112471V11112-192Pl112441V17112493V11112-2153VI112-217'l12-1083PI3VIO112-21I3VI2112-109112-216FiUreD-11RAGEMSSchematic NIAGARAMOHAWKPOWERCORPORATION NINEMILEPOINT-UNIT1OFFSITEDOSECALC.MANUAL128 P+A.JatAt'a'~<<a1 011242FS1143112-1011249AM43A6711266112-11Inlet112-146112-147112-59FL1112-58112-14812-1491126111240u112-137112-152Pl112-uu1126263112-153BA-G-3112-154'l124411245uu112-1611124811244FGV112-91112-137112-163112-134BRG-3PS2114i11-1351'l2-135112-139112-138112-140FS112-94Fl11246TritiumV/Pl1124512-158q112-156112-155112-142l12-141112-22FL3112-20112.2111240112-159112-'157112-3112-19112-112112.14112.1811249112-70112-1512-1112-121124711248FiureD-12OGESMSSchematic NIAGARAMOHAWKPOWERCORPORATION NINEMILEPOINT-UNIT1OFFSITEDOSECALC.MANUAL129-  
'1yl,llif~8J ANMPITNSUPERSKOEQOl4REPLICAGeneralSuperintendentNuclearGenerationK.A.DahlbergforL.Will1s311,2,5,6,8,9,11-13,15-18,36-44,47-49,52-63,65-76,79-81,86-1163,4,7,10,14,20,2327-28,30-3545,46,50,51,82-85*29*64,77,78i,19,21,22A,22B,24,2526,112February1987December1987January1988May1988(Reissue)May27,1988(Reissue)February1990THISPROCEDURENOTTOBEUSEDAFTERMarch1992SUBJECTTOPERIODICREVIEW9PP9110036 e.~lV 1.02.02~1INTRODUCTIONLIQUIDEFFLUENTSSetpointDeterminations2.1.1Basis2.1.2ServiceWaterSystemEffluentAlarmSetpoint2.1.32.1.4LiquidRadwasteEffluentAlarmSetpointDiscussion2.1.4.1ControlofLiquidEffluentBatchDischarges2.1.4.2SimultaneousDischargesofRadioactiveLiquids2.1.4.3SampleRepresentativeness2.1.4.4LiquidRadwasteSystemOperation2.1.4.52.22.32.3.1;3.03.13.1.13.1.23.1.'33.1.43.1.53.1.5.13.1.5.2ServiceWaterSystemContaminationLiquidEffluentConcentrationCalculationDoseDeterminationsMaximumDoseEquivalentPathway"-GASEOUSEFFLUENTSSetpointDeterminationsBasisStackMonitorSetpointsRecombinerDischarge-(OffGas)MonitorSetpointsEmergencyCondenserVentMonitorSetpointDiscussionStackEffluentMonitoringSystemDescriptionStackSampleFlowPath-RAGEHS1012121919192022BI~'324243.1.5.3StackSampleFlowPath-OGESHS26  
'1yl,llif~8J ANMPITNSUPERSKOEQ Ol4REPLICAGeneralSuperintendent NuclearGeneration K.A.DahlbergforL.Will1s311,2,5,6,8,9,11-13,15-18, 36-44,47-49, 52-63,65-76,79-81,86-116 3,4,7,10,14,20,23 27-28,30-35 45,46,50,51,82-85
/jW'-74vv~,lklr~P~Ih4".II<OA TABFT(Cont'd)3,1.5.4SampleFrequency/SampleAnalysis3.1.5.5I-133Estimates3.1.5.6GaseousRadwasteTreatmentSystemOperation2727,283.23.2.1DoseandDose.RateDeterminationDoseRate29313.2.1.1NobleGases3.2.1.2Tritium,IodinesandParticulates'3.'2.2Dose3.2.2.1NobleGasAirDose3.2.2.2Radioiodine,TritiumandParticulates3.2.2.3AccumulatingDoses3.3-"CriticalReceptors323234343637383.44.04.14.24.3'.45.05.15.25.3RefinementofOffsiteDosesResultingFromEmergencyCondenserVentReleases40CFR190REQUIREMENTS-:EvaluationsofDosesFromLiquidEffluentsEvaluationofDosesFromGaseousEffluentsEvaluationofDosesFromDirectRadiationDosestoMembersof,thePublicHithintheSiteBoundaryENVIRONMENTALMONITORINGPROGRAMSamplingStationsInterlaboratoryComparisonProgramCapabilitiesfor'ThermoluminescentDosimetersUsedforEnvironmentalMeasurements.3940'64647525354  
*29*64,77,78 i,19,21,22A,22B,24,25 26,112February1987December1987January1988May1988(Reissue)
'll,F ODCM-NINEMILEPOINTMILE1TABLEOFCONTENTS(Cont'd)~PaeTable1-1Table1-2Table2-1Table3-1Rapj1Values.fortheNMP-1FacilityParametersfortheLiquidEffluentPathwayAverageEnergyPerDisintegrationCriticalReceptorDispersionParametersforGroundLevelandElevatedReleases57585960Table4-1DoseFactorsforNobleGases61-Tables4-2to4-20RValues62Table5-1NMP-1RadiologicalEnvironmentalMonitoringProgremSamplingLocations81AppendixADoseParametersforIodine-131and133,ParticulatesandTritium85AppendixBDiagramsofLiquidsandGaseousRadwasteTreatmentsSystems98AppendixCDispersionCalculationTables109
May27,1988(Reissue)
February1990THISPROCEDURE NOTTOBEUSEDAFTERMarch1992SUBJECTTOPERIODICREVIEW9PP9110036 e.~lV 1.02.02~1INTRODUCTION LIQUIDEFFLUENTS SetpointDeterminations 2.1.1Basis2.1.2ServiceWaterSystemEffluentAlarmSetpoint2.1.32.1.4LiquidRadwasteEffluentAlarmSetpointDiscussion 2.1.4.1ControlofLiquidEffluentBatchDischarges 2.1.4.2Simultaneous Discharges ofRadioactive Liquids2.1.4.3SampleRepresentativeness 2.1.4.4LiquidRadwasteSystemOperation 2.1.4.52.22.32.3.1;3.03.13.1.13.1.23.1.'33.1.43.1.53.1.5.13.1.5.2ServiceWaterSystemContamination LiquidEffluentConcentration Calculation DoseDeterminations MaximumDoseEquivalent Pathway"-GASEOUS EFFLUENTS SetpointDeterminations BasisStackMonitorSetpoints Recombiner Discharge-(Off Gas)MonitorSetpoints Emergency Condenser VentMonitorSetpointDiscussion StackEffluentMonitoring SystemDescription StackSampleFlowPath-RAGEHS1012121919192022BI~'324243.1.5.3StackSampleFlowPath-OGESHS26  
/jW'-74vv~,lklr~P~Ih4".II<OA TABFT(Cont'd)3,1.5.4SampleFrequency/Sample Analysis3.1.5.5I-133Estimates 3.1.5.6GaseousRadwasteTreatment SystemOperation 2727,283.23.2.1DoseandDose.RateDetermination DoseRate29313.2.1.1NobleGases3.2.1.2Tritium,IodinesandParticulates
'3.'2.2Dose3.2.2.1NobleGasAirDose3.2.2.2Radioiodine, TritiumandParticulates 3.2.2.3Accumulating Doses3.3-"CriticalReceptors 323234343637383.44.04.14.24.3'.45.05.15.25.3Refinement ofOffsiteDosesResulting FromEmergency Condenser VentReleases40CFR190REQUIREMENTS
-:Evaluations ofDosesFromLiquidEffluents Evaluation ofDosesFromGaseousEffluents Evaluation ofDosesFromDirectRadiation DosestoMembersof,thePublicHithintheSiteBoundaryENVIRONMENTAL MONITORING PROGRAMSamplingStationsInterlaboratory Comparison ProgramCapabilities for'Thermoluminescent Dosimeters UsedforEnvironmental Measurements.
3940'64647525354  
'll,F ODCM-NINEMILEPOINTMILE1TABLEOFCONTENTS(Cont'd)~PaeTable1-1Table1-2Table2-1Table3-1Rapj1Values.fortheNMP-1FacilityParameters fortheLiquidEffluentPathwayAverageEnergyPerDisintegration CriticalReceptorDispersion Parameters forGroundLevelandElevatedReleases57585960Table4-1DoseFactorsforNobleGases61-Tables4-2to4-20RValues62Table5-1NMP-1Radiological Environmental Monitoring ProgremSamplingLocations 81AppendixADoseParameters forIodine-131and133,Particulates andTritium85AppendixBDiagramsofLiquidsandGaseousRadwasteTreatments Systems98AppendixCDispersion Calculation Tables109
~/~hppV44c~
~/~hppV44c~
1o0INTRODUCTIONTheOffsiteDoseCalculationManual(ODCM)providesthemethodologytobeusedfordemonstratingcompliance"withtheRadiologicalEffluentTechnicalSpecifications(RETS),10CFR20,10CFR50,and40CFR190'hecontentsoftheODCMarebasedonDraftNUREG-0472,Revision3,"StandardRadiologicalEffluentTechnicalSpecificationsforPressurizedWater'eactors,"September1982;DraftNUREG-0473,Revision2,-"Radiological.EffluentTechnicalS'pecificationsforBWR's,"July1979;NUREG0133,"PreparationofRadiologicalEffluentTechnicalSpecificationsforNuclearPowerPlants,"October1978;theseveralRegulatoryGuidesreferencedinthesedocuments;and,communicationwiththeNRCstaff.Section5containsadetaileddescriptionoftheRadiologicalEnvironmentalMonitoring(REM)samplinglocations'houlditbenecessarytorevisetheODCM,theserevisionswillbemadeinaccordancewithTechnicalSpecifications i5iI~fr'4a) 2.0LIQUIDEFFLUENTS2.1SetpointDeterminations2.1.1BasisMonitorsetpointswillbeestablishedsuchthattheconcentrationofradionuclidesintheliquideffluentreleasesinthedischargecanalwillnotexceedthoseconcentrationsasspecifiedin10CFR20,AppendixB,TableII,Column2.SetpointsfortheServiceWaterSystemEffluentLinewillbecalculated'uarterlybasedontheradionuclidesidentifiedduringthepreviousyear'sreleasesfromtheliquidradwastesystemortheisotopesidentifiedinthemostrecentradwastereleaseorotheridentifiedprobablesource.SetpointsfortheLiquidRadwasteEffluentLinewillbebasedontheradionuclidesidentifiedineachbatchofliquidwastepriortoitsrelease.tlAfterrelease,theLiquidRadwastemonitorsetpointmayremainasset,orrevertbacktoasetpointbasedonapreviousSemi-AnnualRadioactiveEffluentReleaseReport,orinstallblankflangeinthedischargelineanddeclareinoperableinaccordance.withthetechnicalspecification.SincetheServiceWaterSystemeffluentmonitorandLiquidRadwasteeffluentmonitorcanonlydetectgammaradiation,thealarmsetpointsarecalculatedby-usingtheconcentrationofgammaemittingisotopesonly(orthecorrespondingMPCvaluesforthesameisotopes,whicheverarehigher)E(Ci/ml)expression(Section2.1.2,2.1.3).-2-inthe Pf1I8~-'f4K 2.1.1(Cont'd)TheRequiredDilutionFactoriscalculatedusingconcentrationsofallisotopespresent(orthecorrespondingMPCvaluesforthesameisotopes,whicheverarehigher)includingtritiumandothernon-gammaemitterstoensurethatallradionuclidesinthedischargecanaldonotexceed10CFR20limits.2.1.2ServiceWaterSystemEffluentLineAlarmSetpointThedetailedmethodsforestablishingsetpointsfortheServiceWaterSystemEffluentLineMonitorshallbecontainedintheNineMilePointStationProcedures.Thesemethodsshallbeinaccordancewiththefollowing:+background(5(liCi/ml)i~concentrationofgammaemittingisotopeiinthesample,orthecorrespondingMPCofgammaemittingisotopei'MPC)i',whicheverishigher(units~uCi/ml)-(vCi/ml)iT~concentrationofanyradioactiveisotopeiinthesampleincludingtritiumandothernon-gammaemittersorcorrespondingMPCofisotopei,MPCi,whicheveris.higher(units~vCi/ml).Setpoint(Hialarm)<0.9z(nCi/ml)iCF)TDF/Fswbackground/Setpoint(Alertalarm)<0.7E(pCi/ml)i(CF)TDF/FswEf(pCi/ml)jT/MPCiJ-TotalDilutionFlow(unitsgallons/min)FswServiceWaterFlow(unitsgallons/min)CF~monitorcalibrationfactor(units~netcpm/uCi/ml)MPCiliquideffluentradioactivityconcentrationslimitforradionuclideiasspecifiedin10CFR20,AppendixB,TableII,Column2.
1o0INTRODUCTION TheOffsiteDoseCalculation Manual(ODCM)providesthemethodology tobeusedfordemonstrating compliance"with theRadiological EffluentTechnical Specifications (RETS),10CFR20,10CFR50,and40CFR190'hecontentsoftheODCMarebasedonDraftNUREG-0472, Revision3,"Standard Radiological EffluentTechnical Specifications forPressurized Water'eactors,"
September 1982;DraftNUREG-0473, Revision2,-"Radiological
.EffluentTechnical S'pecifications forBWR's,"July1979;NUREG0133,"Preparation ofRadiological EffluentTechnical Specifications forNuclearPowerPlants,"October1978;theseveralRegulatory Guidesreferenced inthesedocuments; and,communication withtheNRCstaff.Section5containsadetaileddescription oftheRadiological Environmental Monitoring (REM)samplinglocations'hould itbenecessary torevisetheODCM,theserevisions willbemadeinaccordance withTechnical Specifications i5iI~fr'4a)  
 
==2.0 LIQUIDEFFLUENTS==
2.1SetpointDeterminations 2.1.1BasisMonitorsetpoints willbeestablished suchthattheconcentration ofradionuclides intheliquideffluentreleasesinthedischarge canalwillnotexceedthoseconcentrations asspecified in10CFR20,AppendixB,TableII,Column2.Setpoints fortheServiceWaterSystemEffluentLinewillbecalculated'uarterly basedontheradionuclides identified duringthepreviousyear'sreleasesfromtheliquidradwastesystemortheisotopesidentified inthemostrecentradwastereleaseorotheridentified probablesource.Setpoints fortheLiquidRadwasteEffluentLinewillbebasedontheradionuclides identified ineachbatchofliquidwastepriortoitsrelease.tlAfterrelease,theLiquidRadwastemonitorsetpointmayremainasset,orrevertbacktoasetpointbasedonapreviousSemi-Annual Radioactive EffluentReleaseReport,orinstallblankflangeinthedischarge lineanddeclareinoperable inaccordance.
withthetechnical specification.
SincetheServiceWaterSystemeffluentmonitorandLiquidRadwasteeffluentmonitorcanonlydetectgammaradiation, thealarmsetpoints arecalculated by-usingtheconcentration ofgammaemittingisotopesonly(orthecorresponding MPCvaluesforthesameisotopes, whichever arehigher)E(Ci/ml)expression (Section2.1.2,2.1.3).-2-inthe Pf1I8~-'f4K 2.1.1(Cont'd)TheRequiredDilutionFactoriscalculated usingconcentrations ofallisotopespresent(orthecorresponding MPCvaluesforthesameisotopes, whichever arehigher)including tritiumandothernon-gamma emitterstoensurethatallradionuclides inthedischarge canaldonotexceed10CFR20limits.2.1.2ServiceWaterSystemEffluentLineAlarmSetpointThedetailedmethodsforestablishing setpoints fortheServiceWaterSystemEffluentLineMonitorshallbecontained intheNineMilePointStationProcedures.
Thesemethodsshallbeinaccordance withthefollowing:
+background (5(liCi/ml)i
~concentration ofgammaemittingisotopeiinthesample,orthecorresponding MPCofgammaemittingisotopei'MPC)i',whichever ishigher(units~uCi/ml)-(vCi/ml)iT
~concentration ofanyradioactive isotopeiinthesampleincluding tritiumandothernon-gamma emittersorcorresponding MPCofisotopei,MPCi,whichever is.higher(units~vCi/ml).Setpoint(Hialarm)<0.9 z(nCi/ml)i CF)TDF/Fswbackground
/Setpoint(Alertalarm)<0.7 E(pCi/ml)i (CF)TDF/FswEf(pCi/ml)jT/MPCiJ-TotalDilutionFlow(unitsgallons/min)
FswServiceWaterFlow(unitsgallons/min)
CF~monitorcalibration factor(units~netcpm/uCi/ml)
MPCiliquideffluentradioactivity concentrations limitforradionuclide iasspecified in10CFR20,AppendixB,TableII,Column2.
gJ'V-'lka~'QW.P''llsling~tgkrq4/5  
gJ'V-'lka~'QW.P''llsling~tgkrq4/5  
~~~2.1.2Sample(VpC)iO.aand0.7(Cont'd)ThosenuclidespresentinthepreviousbatchreleasefromtheliquidradwasteeffluentsystemorthosenuclidespresentinthelastSemi-annualRadioactiveEffluentReleaseReport(units~pCi/ml)orthosenuclidespresentintheservicewatersystem.**sameasMPCibutforgammaemittingnuclidesonly.~factorsofconservatismtoaccountforinaccuracies.,Tf(uCi/ml)iT/MPCi]RequiredDilutionFactor.IfMPCvaluesareusedinthe~(uCi/ml)i,theymustalsobeusedincalculatingRDF(numerator).)sTDF/Fsw~ActualDilutionFactor*+ForperiodswithknownreactorwatertoRCLCsystemleakage,RCLCmaximumpermissibleconcentrationmaybeprudentlysubstitutedfortheabove.2-1.3LiquidRadwasteEffluentLineAlarmSetpointThedetailedmethodsforestablishingsetpointsfortheLiquidRadwasteEffluentLineMonitorshallbecontainedin'theNineMilePointStationProcedures.Thesemethodsshallbeinaccordancewiththefollowing:Setpoint(Hi-Hialarm)<0.9>(uCi/ml)i(CF)TDF/FxeZ[(pCi/ml)iT/MPCi]+backgroundSetpoint(Hialarm)<0'7(pCi/ml)i(CF)TDF/Fre+backgroundZ[(vCi/ml)jT/MPCj](vCi/ml)i~concentrationofgammaemittingisotopeiinthesampleor,thecorrespondingMPCofgammaemittingisotopei(MPC)i~whicheverishigher.(<<Ci/ml)iT~concentrationofanyradioactiveisotopeiinthesampleincludingtritiumandothernon-gammaemittersorthecorrespondingMPCofisotopeiMPCiwhicheverishigher.(units~pCi/ml)'TDF~TotalDilutionFlow(units~gallons/min)FreCFRadwasteEffluentFlow(units~gallons/min)monitorcalibrationfactor(units~netcps/pCi/ml) hn44s MPCiliquideffluentradioactivityconcentrationlimitfor'radionuclide,iasspecifiedin10CFR20,AppendixB,TableII,Column2,forthosenuclidesdetectedbyspectralanalysisofthecontentsoftheradwastetankstobereleased.(units~yCi/ml)(MPC)ig~sameasMPCibutforgammaemittingnuclideonly.0.9=and0.7~factorsof.conservatism.,to.account.forinaccuracies.f(uCi/ml)iT/MPCij~RequiredDilutionFactor.*IfMPCvaluesareusedintheE(uCi/ml)i,theymustalsobeusedincalculatingRDF(numerator).Notes:(a)IfTDF/Fre~E[(pCi/ml)iT/MPCi]thedischargecouldnotbemade,sincethemonitorwouldbe;continuouslyinalarm.Toavoidthissituation,Fwillrebereduced(normallybyafactorof2)toallowsettingthealarmpointataconcentrationhigherthantankconcentration.Thiswillalsoresultinadischargecanal'concentrationatapproximately50'aximumpermissibleconcentration.(b)ThevalueusedforTDFwillbereducedbythefractional'uantity(1-FT),whereFTistemperingfraction(i.e.,diversionofsomefractionofdischargeflowtotheintakecanalforthepurposeoftemperaturecontrol).  
~~~2.1.2Sample(VpC)iO.aand0.7(Cont'd)ThosenuclidespresentinthepreviousbatchreleasefromtheliquidradwasteeffluentsystemorthosenuclidespresentinthelastSemi-annual Radioactive EffluentReleaseReport(units~pCi/ml)orthosenuclidespresentintheservicewatersystem.**
$/P,q*v*4$'.gor.ka 2.1.4Discussion2.1.4.1ControlofLiquidEffluentBatchDischargesAtNineMilePointUnit1LiquidRadwasteEffluentsarereleasedonlyonabatchmode.Topreventtheinadvertentreleaseofanyliquidradwasteeffluents,radwastedischargeismechanicallyisolated(blankflangeinstalledordischargevalvechain-lockedclosed)followingthecompletionofabatchreleaseorseriesofbatchreleases.Thismechanicalisolationremainsin.placeandwillonlyberemovedpriortothenextseriesofliquidradwastedischargesafterallanalysesrequiredinstationproceduresandTechnicalSpecificationTable4.6.15-1Aareperformedandmonitorsetpointshavebeenproperlyadjusted.2.1.4.2SimultaneousDischargesofRadioactiveLiquids.Ifduring,thedischargeofanyliquidradwastebatch,thereisanindicationthattheservicewatercanalhasbecomecontaminated(throughaservicewatermonitoralarmorthroughagrabsampleanalysisintheeventthattheservicewatermonitor.isinoperable),'thedischargeshallbeterminatedimmediately.The'liquidradwastedischargeshallnotbecontinueduntilthecauseoftheservicewateralarm(orhighgr'absampleanalysisresult)hasbeendeterminedandtheappropriatecorrectivemeasurestakentoensurelOCFR20,AppendixB,TableII,Column2(TechnicalSpecificationSection3.6.15.a(1))limitsarenotexceeded.
sameasMPCibutforgammaemittingnuclidesonly.~factorsofconservatism toaccountforinaccuracies.,
ir->i~+~C 2.1.4.3SamplingRepresentativeness:-ThissectioncoversTechnicalSpecificationTable4.6.15-1Notebconcerningthoroughlymixingofeachbatchofliquidradwastepriortosampling.LiquidRadwasteTanksscheduledfordischarge-atNineMilePointUnit1areisolated(i.e.inletvalvesmarkedup)andatleasttwotankvolumesofentrainedfluidsarerecirculatedpriortosampling.Minimumrecirculationtimeiscalculatedasfollows:'-MinimumRecirculationTime2.0(T/R)Where:2.0Plantestablishedmixingfactor,unitlessTankvolume,galRecirculationflowrate,gpm.Additionally,theHiAlarmsetpointoftheLiquidRadwasteEffluentRadiationMonitorissetatavaluecorrespondingtonotmorethan70XofitscalculatedresponsetothegrabsampleorcorrespondingMPCvalues.Thus,thisradiationmonitorwillalarmifthegrabsample,orcorrespondingMPCvalue,issignificantlylowerinactivitythananypartofthetankcontentsbeingdischarged.
Tf(uCi/ml)iT/MPCi]RequiredDilutionFactor.IfMPCvaluesareusedinthe~(uCi/ml)i, theymustalsobeusedincalculating RDF(numerator).
J~,yi~,~~~~y>~Qy~i~f-'~',"">"'~c"~~S,+i 2.1.4.4LiquidRadwasteSystemsOperationTechnicalSpecification3.6.16.arequiresthattheliquidradwastesystemshallbeusedtoreducetheradioactivematerialsinliquid~astespriortotheirdischarge,asnecessary,tomeettheconcentrationanddoserequirementsofTechnicalSpecification3.6.15~"Utilizationoftheradwastesystemwillbebasedonthecapabilityoftheindicatedcomponentsofeachprocesssystemtoprocesscontentsoftherespectivelowconductivityandhighconductivitycollectiontanks:1)LowConductivity(EquipmentDrains):RadwasteFilterandRadwasteDemin.(SeeFig.B-1)2)HighConductivity(FloorDrains):WasteEvaporator(seeFig.~B-1)"-'"''>>""'>'Cumulative.dosecontributionsfromliquideffluentsforthecurrentcalendarquarterandthecurrentcalendaryearshallbedeterminedasdescribedinSection2.3ofthismanualpriortothereleaseofeachbatchof.liquid-waste.ThissamedoseprojectionofSection2.3willalsobeperformedintheeventthatuntreatedliquidwasteis=.discharged,toensurethatthedoselimitsofTechnicalSpecification3.6.15.a(2)arenotexceeded.(Therebyimplementingtherequirementsof10CFR50.36a,GeneralDesignCriteria60ofAppendixAandtheDesignObjectivegiveninSectionII-DofAppendixIto10CFR50).
)sTDF/Fsw~ActualDilutionFactor*+ForperiodswithknownreactorwatertoRCLCsystemleakage,RCLCmaximumpermissible concentration maybeprudently substituted fortheabove.2-1.3LiquidRadwasteEffluentLineAlarmSetpointThedetailedmethodsforestablishing setpoints fortheLiquidRadwasteEffluentLineMonitorshallbecontained in'theNineMilePointStationProcedures.
1pCcI.-,"1,P4g>>$CW41~~"k,*fdic'II 2.1.4.4(Cont'd)Forthepurposeofdoseprojection,thefollowingassumptionsshallbemadewithregardtoconcentrationsofnon-gammaemittingradionuclidessubsequentlyanalyzedoff-site:a)[H-3]>H-3Concentrationfoundrecentcondensatestoragetankanalysis.b)[Sr-89]>4xCs-137Concentrationc)[Sr-90]>0.5xCs-137Concentrationd)[Fe-55]>1xCo-60ConcentrationAssumedScalingFactorsusedinb,c,anddabove.representconservativeestimatesderivedfromanalysisofhistoricaldatafromprocesswastestreams.Followingreceiptofoff-siteH-3,Sr-89,Sr-90andFe-55analysisinformation,doseestimatesshallberevisedusingactualradionuclideconcentrationsandactualtankvolumesdischarged.
Thesemethodsshallbeinaccordance withthefollowing:
4g!Pa 2.1.4.5ServiceWaterSystemContaminationServicewateris"normallynon-radioactive.Ifcontaminationissuspected,asindicatedbyasfgnificantincreaseinservicewatereffluentmonitorresponse,grabsampleswillbeobtainedfromtheservicewaterdischargelinesandagammaisotopicanalysismeetingtheLLDrequirementsofTechnicalSpecificationTable4.6.15-1completed.If'itis'determinedthataninadvertentradioactivedischargeisoccurringfromtheservicewatersystem,then:a)A50.59safetyevaluationshallbeperformed(ref.IGEBulletin'0-10),b)Dailyservicewatereffluentsamplesshallbetakenandanalyzedforprincipalgammaemittersuntilthereleaseisterminated,Hc)AnincidentcompositeshallbepreparedforH-3,grossalpha,Sr-89,Sr-90andFe-55analysesandd)DoseprojectionsshallbeperformedinaccordancewithSection2.3ofthismanual(usingestimatedconcentrationsforH-3,Sr-89,Sr-90andFe-55tobeconservativelydeterminedby=supervisionatthe.timeoftheincident).Additionally,servicewatereffluentmonitorsetpointsmayberecalculatedusingtheactualdistributionofisotopesfoundfromsampleanalysis.
Setpoint(Hi-Hialarm)<0.9>(uCi/ml)i (CF)TDF/FxeZ[(pCi/ml)iT/MPCi]
aAVCVCtlJQI 2.2LiquidEffluentConcentrationCalculationThiscalculationdocumentscompliancewithTechnicalSpecificationSection3.6.1.5.a(1).Theconcentrationofradioactivematerialreleasedinliquideffluentstounrestrictedareas(seeFigureB-7)shallbelimitedto.theconcentrationsspecifiedin10CFR20,AppendixB,TableII,Column2,forradionuclidesotherthandissolvedorentrainednoblegases.Fordissolvedorentrainednoblegases,theconcentrationshallbelimitedto2E-4microcurie/mltotalactivity.TheconcentrationofradioactivityfromLiquidRadwastebatchreleasesand,ifapplicable,ServiceWaterSysteminadvertentdischargesareincludedinthecalculation.Thecalculationisperformedforaspecificperiod,oftime.Nocredittakenforaveragingoverthecalendaryearaspermittedby10CFR20.106.The"limitingconcentrationiscalculatedasfollows:MPCFraction~E.[Z((yCi/ml)~F)/(MPCI(F))l1sississWhere:MPCFraction~Thelimitingconcentrationof10CFR20,AppendixB,TableII,forradionuclidesotherthandissolvedorentrainednoblegases.Fornoblegases,theconcentrationshallbelimitedto28-4microcurie/mltotalactivity.
+background Setpoint(Hialarm)<0'7(pCi/ml)i (CF)TDF/Fre+background Z[(vCi/ml)jT/MPCj](vCi/ml)i
p45.i;fC4j 2.2(Cont'd)(<<Ci/ml)isFsMPCiZ((ICi/ml)"F)sissTheconcentrationofnuclideiin.particulareffluentstreams,uCi/ml.Theflowrateofaparticulareffluentstreams,gpm.Thelimitingconcentrationofaspecificnuclideifrom10CFR20,Appendixb,TableII,Column2(noblegaslimitis2E-4pCi/ml)Thetotalactivityrateofnuclidei,inalleffluentstreamss,pCi/ml"gpm~Thetotalflowrateofalleffluentstreamss,gpm(includingthosestreamswhichdonotcontainradioactivity).A.valueoflessthanoneforMPCfractionis'consideredacceptableforcompliancewithTechnicalSpecificationSection3.6.15.a.(1).2.3DoseDetermination2.3.1MaximumDoseEquivalentPathway.AdoseassessmentreportwaspreparedfortheNineMilePointUnit1facilitybyCharlesT.Main,Inc.,ofBoston,MA.Thisreportpresentedthecalculateddoseequivalentratestoindividualsaswellasthepopulationwithina50~ileradiusofthefacilitybasedontheradionuclidesreleasedinliquidandgaseouseffluentsduringthetimeperiodsof1.July1980"through31December1980and.from,.lJanuary'1981through"'31'December:1981.Utilizingthe.effluent.data  
~concentration ofgammaemittingisotopeiinthesampleor,thecorresponding MPCofgammaemittingisotopei(MPC)i~whichever ishigher.(<<Ci/ml)iT
+CDlil'w'Ifqvvg~Ayppeg~-(yis'tA8~>5',"vk 2.3.1(Cont'd)containedintheSemi-AnnualRadioactiveEffluentReleaseReportsassourceterms,doseequivalentratesweredeterminedusingthe'environmentalpathwaymodels-specifiedinRegulatoryGuides1.109and'.111asincorporated-intheNRCcomputercodesLADTAPforliquidpathways,andXOQDOQand"GASPARforgaseous-effluentpathways.Dose=.equivalentrateswere'calculatedforthetotalbodyaswellassevenorgansand/ortissuesforadults,teenagers,children,andinfants.Fromthestandpointofliquideffluents,thepathwaysevaluatedincludedfishingestion,drinkingwater,andexternalexposuretowaterandsediment.Basedonthefindingsoftheabovereferencedreport,themaximum''total.bodydosefromallliquidpathwaysisreceivedbyanadult.Similarly,themaximumtotaldosetoanyorganisreceivedbytheteenliver.Inbothofthesecases(i.e.,adultwholebodydoseandteenliverdose),99Kand98Krespectivelyofthesedoseswere"'""-~-".~"'received.via.thefishingestionpathway.Inordertodeterminethedosecontributionfromthereleaseofliquid,effluents,the'nnualdose,to.anadultwholebodyanda,teenliverwillbecalculatedfor"eachof,thesignificantnuclides,(see..Table1-1)identifiedintheliquidwastebasedonthefishingestionpathwayutilizingthefollowingformula:R..~1100UMZB.D..(-g.t)/FapjiapPipaipjexpip yt,t'.'fjltIK WhereRtotalannualdose(perCuriereleased)toorgan"j"ofindividualsofagegroup"a"fromallofthenuclides"i"inpathway"p"(units~mrem/year-Ci)tJapusagefactorspecifyingtheexposuretimeor,intakerateforanindividualofanagegroup"a"associatedwithpathway"p"(unitskg/year)mixingrates(reciprocalofdilutionfactor)at'thepointofexposureorpointofharvest(units~dimensionless)flowrateoftheliquideffluent(unitsft/sec)3ipequilibriumbioaccumulationfactorfornuclide"i"inpathway"p"'units~liters/kg)Daipjthedosefactor,specifictoaspecificagegroup,'"a",radionuclide"i",pathway"p",andorgan"j",whichcanbeutilizedtocalculatetheradiationdosefromanintakeofaradionuclide(units~mrem/pCi)radioactivedecayconstantofnuclide"i"(units-1~hours) k4i'yl~r+IIcdMINIpI theaveragetransittimerequiredfornuclidestoreachthepointofexposure.Forinternaldose,tisthetotaltimeelapsedbetweenthePreleaseofthenuclidesandtheingestionoftheEoodand/orwater(units~hours)1100~factortoconvertfrom(Ci/year)/(Et/sec)topCi/liter3ValuesforRiarecontainedinTable1-1.AllofthesevaluesapjiofR.iareonaperCuriebasisforeachofthenuclidesapjireleased.Table1-2indicatesthoseparametersusedforselectedEactorsoftheformula.Priortoeachradioactiveliquiddischarge,eachliquidwastetanktobedischargedwillbeanalyzedforisotopecontentutilizingagammaspectroscopysystem.Onthebasisofthisanalysis,projecteddoses,toanadultwholebodyandateenliverwillbecalculatedusingthefollowingrelationships:PDi,1.05Rji()CiPDLi1.05Rji(L)CWherePDProjecteddoseexpectedtothewholebodyofanadultduetothereleaseoftheidentifiedconcentrationofnuclide"i".(units~mrem/year)  
~concentration ofanyradioactive isotopeiinthesampleincluding tritiumandothernon-gamma emittersorthecorresponding MPCofisotopeiMPCiwhichever ishigher.(units~pCi/ml)'TDF~TotalDilutionFlow(units~gallons/min)
FreCFRadwasteEffluentFlow(units~gallons/min) monitorcalibration factor(units~netcps/pCi/ml) hn44s MPCiliquideffluentradioactivity concentration limitfor'radionuclide,i asspecified in10CFR20,AppendixB,TableII,Column2,forthosenuclidesdetectedbyspectralanalysisofthecontentsoftheradwastetankstobereleased.
(units~yCi/ml)(MPC)ig~sameasMPCibutforgammaemittingnuclideonly.0.9=and0.7~factorsof.conservatism
.,to.account.forinaccuracies.
f(uCi/ml)iT/MPCij
~Required DilutionFactor.*IfMPCvaluesareusedintheE(uCi/ml) i,theymustalsobeusedincalculating RDF(numerator).
Notes:(a)
IfTDF/Fre~E[(pCi/ml)iT/MPCi]
thedischarge couldnotbemade,sincethemonitorwouldbe;continuously inalarm.Toavoidthissituation, Fwillrebereduced(normally byafactorof2)toallowsettingthealarmpointataconcentration higherthantankconcentration.
Thiswillalsoresultinadischarge canal'concentration atapproximately 50'aximum permissible concentration.
(b)ThevalueusedforTDFwillbereducedbythefractional
'uantity(1-FT),whereFTistempering fraction(i.e.,diversion ofsomefractionofdischarge flowtotheintakecanalforthepurposeoftemperature control).  
$/P,q*v*4$'.gor.ka 2.1.4Discussion 2.1.4.1ControlofLiquidEffluentBatchDischarges AtNineMilePointUnit1LiquidRadwasteEffluents arereleasedonlyonabatchmode.Topreventtheinadvertent releaseofanyliquidradwasteeffluents, radwastedischarge ismechanically isolated(blankflangeinstalled ordischarge valvechain-locked closed)following thecompletion ofabatchreleaseorseriesofbatchreleases.
Thismechanical isolation remainsin.placeandwillonlyberemovedpriortothenextseriesofliquidradwastedischarges afterallanalysesrequiredinstationprocedures andTechnical Specification Table4.6.15-1A areperformed andmonitorsetpoints havebeenproperlyadjusted.
2.1.4.2Simultaneous Discharges ofRadioactive Liquids.Ifduring,thedischarge ofanyliquidradwastebatch,thereisanindication thattheservicewatercanalhasbecomecontaminated (throughaservicewatermonitoralarmorthroughagrabsampleanalysisintheeventthattheservicewatermonitor.isinoperable),
'thedischarge shallbeterminated immediately.
The'liquid radwastedischarge shallnotbecontinued untilthecauseoftheservicewateralarm(orhighgr'absampleanalysisresult)hasbeendetermined andtheappropriate corrective measurestakentoensurelOCFR20,AppendixB,TableII,Column2(Technical Specification Section3.6.15.a(1))
limitsarenotexceeded.
ir->i~+~C 2.1.4.3SamplingRepresentativeness
:-ThissectioncoversTechnical Specification Table4.6.15-1Notebconcerning thoroughly mixingofeachbatchofliquidradwastepriortosampling.
LiquidRadwasteTanksscheduled fordischarge-at NineMilePointUnit1areisolated(i.e.inletvalvesmarkedup)andatleasttwotankvolumesofentrained fluidsarerecirculated priortosampling.
Minimumrecirculation timeiscalculated asfollows:'-MinimumRecirculation Time2.0(T/R)Where:2.0Plantestablished mixingfactor,unitlessTankvolume,galRecirculation flowrate,gpm.Additionally, theHiAlarmsetpointoftheLiquidRadwasteEffluentRadiation Monitorissetatavaluecorresponding tonotmorethan70Xofitscalculated responsetothegrabsampleorcorresponding MPCvalues.Thus,thisradiation monitorwillalarmifthegrabsample,orcorresponding MPCvalue,issignificantly lowerinactivitythananypartofthetankcontentsbeingdischarged.
J~,yi~,~~~~y>~Qy
~i~f-'~',"">"'~c"~~S,+i 2.1.4.4LiquidRadwasteSystemsOperation Technical Specification 3.6.16.arequiresthattheliquidradwastesystemshallbeusedtoreducetheradioactive materials inliquid~astespriortotheirdischarge, asnecessary, tomeettheconcentration anddoserequirements ofTechnical Specification 3.6.15~"Utilization oftheradwastesystemwillbebasedonthecapability oftheindicated components ofeachprocesssystemtoprocesscontentsoftherespective lowconductivity andhighconductivity collection tanks:1)LowConductivity (Equipment Drains):RadwasteFilterandRadwasteDemin.(SeeFig.B-1)2)HighConductivity (FloorDrains):WasteEvaporator (seeFig.~B-1)
"-'"''>>""'>'Cumulative
.dosecontributions fromliquideffluents forthecurrentcalendarquarterandthecurrentcalendaryearshallbedetermined asdescribed inSection2.3ofthismanualpriortothereleaseofeachbatchof.liquid-waste.Thissamedoseprojection ofSection2.3willalsobeperformed intheeventthatuntreated liquidwasteis=.discharged, toensurethatthedoselimitsofTechnical Specification 3.6.15.a(2) arenotexceeded.
(Therebyimplementing therequirements of10CFR50.36a, GeneralDesignCriteria60ofAppendixAandtheDesignObjective giveninSectionII-DofAppendixIto10CFR50).
1pCcI.-,"1,P4g>>$CW41~~"k,*fdic'II 2.1.4.4(Cont'd)Forthepurposeofdoseprojection, thefollowing assumptions shallbemadewithregardtoconcentrations ofnon-gamma emittingradionuclides subsequently analyzedoff-site:
a)[H-3]>H-3Concentration foundrecentcondensate storagetankanalysis.
b)[Sr-89]>4xCs-137Concentration c)[Sr-90]>0.5xCs-137Concentration d)[Fe-55]>1xCo-60Concentration AssumedScalingFactorsusedinb,c,anddabove.represent conservative estimates derivedfromanalysisofhistorical datafromprocesswastestreams.Following receiptofoff-siteH-3,Sr-89,Sr-90andFe-55analysisinformation, doseestimates shallberevisedusingactualradionuclide concentrations andactualtankvolumesdischarged.
4g!Pa 2.1.4.5ServiceWaterSystemContamination Servicewateris"normally non-radioactive.
Ifcontamination issuspected, asindicated byasfgnificant increaseinservicewatereffluentmonitorresponse, grabsampleswillbeobtainedfromtheservicewaterdischarge linesandagammaisotopicanalysismeetingtheLLDrequirements ofTechnical Specification Table4.6.15-1completed.
If'itis'determined thataninadvertent radioactive discharge isoccurring fromtheservicewatersystem,then:a)A50.59safetyevaluation shallbeperformed (ref.IGEBulletin'0-10),b)Dailyservicewatereffluentsamplesshallbetakenandanalyzedforprincipal gammaemittersuntilthereleaseisterminated, Hc)Anincidentcomposite shallbepreparedforH-3,grossalpha,Sr-89,Sr-90andFe-55analysesandd)Doseprojections shallbeperformed inaccordance withSection2.3ofthismanual(usingestimated concentrations forH-3,Sr-89,Sr-90andFe-55tobeconservatively determined by=supervision atthe.timeoftheincident).
Additionally, servicewatereffluentmonitorsetpoints mayberecalculated usingtheactualdistribution ofisotopesfoundfromsampleanalysis.
aAVCVCtlJQI 2.2LiquidEffluentConcentration Calculation Thiscalculation documents compliance withTechnical Specification Section3.6.1.5.a (1).Theconcentration ofradioactive materialreleasedinliquideffluents tounrestricted areas(seeFigureB-7)shallbelimitedto.theconcentrations specified in10CFR20,AppendixB,TableII,Column2,forradionuclides otherthandissolved orentrained noblegases.Fordissolved orentrained noblegases,theconcentration shallbelimitedto2E-4microcurie/ml totalactivity.
Theconcentration ofradioactivity fromLiquidRadwastebatchreleasesand,ifapplicable, ServiceWaterSysteminadvertent discharges areincludedinthecalculation.
Thecalculation isperformed foraspecificperiod,oftime.Nocredittakenforaveraging overthecalendaryearaspermitted by10CFR20.106.
The"limitingconcentration iscalculated asfollows:MPCFraction~E.[Z
((yCi/ml)
~F)/(MPCI(F))l1sississWhere:MPCFraction~Thelimitingconcentration of10CFR20,AppendixB,TableII,forradionuclides otherthandissolved orentrained noblegases.Fornoblegases,theconcentration shallbelimitedto28-4microcurie/ml totalactivity.
p45.i;fC4j 2.2(Cont'd)(<<Ci/ml)isFsMPCiZ((ICi/ml)
"F)sissTheconcentration ofnuclideiin.particular effluentstreams,uCi/ml.Theflowrateofaparticular effluentstreams,gpm.Thelimitingconcentration ofaspecificnuclideifrom10CFR20,Appendixb,TableII,Column2(noblegaslimitis2E-4pCi/ml)Thetotalactivityrateofnuclidei,inalleffluentstreamss,pCi/ml"gpm
~Thetotalflowrateofalleffluentstreamss,gpm(including thosestreamswhichdonotcontainradioactivity).
A.valueoflessthanoneforMPCfractionis'considered acceptable forcompliance withTechnical Specification Section3.6.15.a.(1).
2.3DoseDetermination 2.3.1MaximumDoseEquivalent Pathway.Adoseassessment reportwaspreparedfortheNineMilePointUnit1facilitybyCharlesT.Main,Inc.,ofBoston,MA.Thisreportpresented thecalculated doseequivalent ratestoindividuals aswellasthepopulation withina50~ileradiusofthefacilitybasedontheradionuclides releasedinliquidandgaseouseffluents duringthetimeperiodsof1.July1980"through31December1980and.from,.lJanuary'1981through"'31'December:1981.
Utilizing the.effluent.
data  
+CDlil'w'Ifqvvg~Ayp peg~-(yis'tA8~>5',"vk 2.3.1(Cont'd)contained intheSemi-Annual Radioactive EffluentReleaseReportsassourceterms,doseequivalent ratesweredetermined usingthe'environmental pathwaymodels-specified inRegulatory Guides1.109and'.111asincorporated
-intheNRCcomputercodesLADTAPforliquidpathways, andXOQDOQand"GASPARforgaseous-effluent pathways.
Dose=.equivalent rateswere'calculated forthetotalbodyaswellassevenorgansand/ortissuesforadults,teenagers,
: children, andinfants.Fromthestandpoint ofliquideffluents, thepathwaysevaluated includedfishingestion, drinkingwater,andexternalexposuretowaterandsediment.
Basedonthefindingsoftheabovereferenced report,themaximum''total.bodydosefromallliquidpathwaysisreceivedbyanadult.Similarly, themaximumtotaldosetoanyorganisreceivedbytheteenliver.Inbothofthesecases(i.e.,adultwholebodydoseandteenliverdose),99Kand98Krespectively ofthesedoseswere"'""-~-".~"'received.via.the fishingestion pathway.Inordertodetermine thedosecontribution fromthereleaseofliquid,effluents, the'nnual dose,to.an adultwholebodyanda,teenliverwillbecalculated for"eachof,thesignificant
: nuclides, (see..Table1-1)identified intheliquidwastebasedonthefishingestion pathwayutilizing thefollowing formula:R..~1100UMZB.D..(-g.t)/FapjiapPipaipjexpip yt,t'.'fjltIK WhereRtotalannualdose(perCuriereleased) toorgan"j"ofindividuals ofagegroup"a"fromallofthenuclides"i"inpathway"p"(units~mrem/year
-Ci)tJapusagefactorspecifying theexposuretimeor,intakerateforanindividual ofanagegroup"a"associated withpathway"p"(unitskg/year)mixingrates(reciprocal ofdilutionfactor)at'thepointofexposureorpointofharvest(units~dimensionless) flowrateoftheliquideffluent(unitsft/sec)3ipequilibrium bioaccumulation factorfornuclide"i"inpathway"p"'units~liters/kg)
Daipjthedosefactor,specifictoaspecificagegroup,'"a",radionuclide "i",pathway"p",andorgan"j",whichcanbeutilizedtocalculate theradiation dosefromanintakeofaradionuclide (units~mrem/pCi) radioactive decayconstantofnuclide"i"(units-1~hours) k4i'yl~r+IIcdMINIpI theaveragetransittimerequiredfornuclidestoreachthepointofexposure.
Forinternaldose,tisthetotaltimeelapsedbetweenthePreleaseofthenuclidesandtheingestion oftheEoodand/orwater(units~hours)1100~factortoconvertfrom(Ci/year)/(Et
/sec)topCi/liter 3ValuesforRiarecontained inTable1-1.AllofthesevaluesapjiofR.iareonaperCuriebasisforeachofthenuclidesapjireleased.
Table1-2indicates thoseparameters usedforselectedEactorsoftheformula.Priortoeachradioactive liquiddischarge, eachliquidwastetanktobedischarged willbeanalyzedforisotopecontentutilizing agammaspectroscopy system.Onthebasisofthisanalysis, projected doses,toanadultwholebodyandateenliverwillbecalculated usingthefollowing relationships:
PDi,1.05Rji()CiPDLi1.05Rji(L)CWherePDProjected doseexpectedtothewholebodyofanadultduetothereleaseoftheidentified concentration ofnuclide"i".(units~mrem/year)  
~M'C<'QteP,ty~\0~~
~M'C<'QteP,ty~\0~~
PDProjecteddoseexpectedtotheliverofateenagerduetothereleaseoftheidentifiedconcentrationofnuclide"i"(units~mrem/yearR..(WB)apj1totalannualdose(perCuriereleased)tothewholebodyofanadultcausedbytheingestionofnuclide"i"(units~mrem/year-Curie)R.(L)apjitotalannualdose(perCuriereleased)totheliverofateenagercausedbytheingestionofnuclide"i"(units.~mrem/year-Curie)cquanityofnuclide"i"identifiedaspresentintherelease(units~Curies)1.05~correctionfactortoaccountfor100%ofdose,assumingthat95%ofdosereceivedisdeliveredviathefishingestionpathway.Thevalueof1.05isusedintheequationasaconservativefactortoincreasetheprojecteddosefromananticipatedreleaseto100%.Aslongasthe1.05factorisused,dosesreceivedviathedrinkingwaterpathway(eg,tritium)neednotbeaccountedforseparately.
PDProjected doseexpectedtotheliverofateenagerduetothereleaseoftheidentified concentration ofnuclide"i"(units~mrem/year R..(WB)apj1totalannualdose(perCuriereleased) tothewholebodyofanadultcausedbytheingestion ofnuclide"i"(units~mrem/year-Curie)
r+IEjatl,,'i Allpro5ecteddosescalculatedinthismannerforeachbatchofliquideffluentwillbe'ummedforcomparisonwithquarterlyandannuallimits,addedtothedosesaccumulatedfromotherreleasesin'hequarterandyearofinterest.Inallcases,thefollowingrelationshipswillhold-Foracalendarquarter:D<1.5mremtotal.bodyrD<5mremforanyorgant-Forthecalendaryear:D<3.0mremtotalbody'-D<10mremforanyorganwhereDtotaldosereceivedduetoliquideffluentreleasesIftheselimitsareexceeded,aspecialreportwillbesubmittedtotheNRCidentifyingthecause'andproposedcorrective'actions.Inaddition,iftheselimitsareexceededbyafactoroftwo,calculationsshallbemadetodetermineifthedoselimits-containedin"40CPR190have.beenexceeded.Doselimits,ascontainedin40CFR190aretotalbodyandorgandosesof25mremperyearandathyroiddoseof75mremperyear.
R.(L)apjitotalannualdose(perCuriereleased) totheliverofateenagercausedbytheingestion ofnuclide"i"(units.~mrem/year-Curie) cquanityofnuclide"i"identified aspresentintherelease(units~Curies)1.05~correction factortoaccountfor100%ofdose,assumingthat95%ofdosereceivedisdelivered viathefishingestion pathway.Thevalueof1.05isusedintheequationasaconservative factortoincreasetheprojected dosefromananticipated releaseto100%.Aslongasthe1.05factorisused,dosesreceivedviathedrinkingwaterpathway(eg,tritium)neednotbeaccounted forseparately.
r,'IP 2.3.1(Cont'd)Thesecalculationswillincludedosesasaresultofliquidandgaseouspathwaysaswellasdosesfromdirectradiation.Liquid,gaseousanddirectradiationpathwaydoseswillconsidertheJamesA.FitzpatrickandNineMilePointUnitIIfacilitiesaswellasNineMilePointUnitINuclearStation.Inthe'event-thecalculationsdemonstratethatthe40CFR190doselimits,asdefinedabove,havebeenexceeded,thenareportshallbepreparedandsubmittedtotheCommissionwithin30daysasspecifiedinSection3.6.15.doftheTechnicalSpecifications.~:"'"Section4.0ofthe'DCMcontainsmoreinformationconcerningcalculationsforanevaluation,of=whether40CFR190limits.havebeenexceeded.
r+IEjatl,,'i Allpro5ected dosescalculated inthismannerforeachbatchofliquideffluentwillbe'ummedforcomparison withquarterly andannuallimits,addedtothedosesaccumulated fromotherreleasesin'hequarterandyearofinterest.
QtpN@i 3.0GASEOUSEFFLUENTS3.lSetpointDeterminations3.1.1Bas1sStackgasandoffgasmonitorsetpointswillbeestablishedsuchthattheinstantaneousreleaserateofrad1oactivematerialsingaseouseffluentsdoesnotexceedthe10CFR20limitsforannualreleaserate.Thesetpointswillbeactivatediftheinstantaneousdoserateatorbeyondthe(land)s1teboundarywouldexceed500mrem/yrtothewholebodyor3000mrem/yrtotheskinfromthecontinuousreleaseofradioactivenoblegas1nthegaseouseffluent.Emergencycondenserventmonitorsetpointswillbeestablishedsuchthatthereleaserateforradioactivematerialsingaseouseffluentsdonotexceedthe10CFR20limitsforannualreleaserateoverthepro)ectedlongestperiodofrelease.Monitorsetpointsfromcontinuousreleasepointsw111bedeterminedonceperquarterundernormalreleaseratecond1tionsandwillbebasedontheisotopiccompositionoftheactualreleaseinprogress,oranoffgasisotopicdistribution,oramoreconservativedefaultcompos1tionspecif1edinthepertinentprocedure.Ifthecalculated"setpoint's'higherthantheexistingsetpoint,itisnotmandatorythatthesetpointbechanged.Monitorsetpointsforemergencycondenserventmonitorsare'conservativelyf1xedat5mr/hrforreasonsdescribedinSections3.1.4and.thereforedonotrequire.per1odicrecalculations.Underabnormalsitereleaserateconditions,monitoralarmsetpointsfromcontinuousreleasepointswillberecalculatedand,ifnecessary,resetatmorefrequentintervalsasdeemednecessarybyCORMSuperv1sion.Inpart1cular,contr1butionsfrombothJAFand'MP-2andtheEmergencyCondenserVentsshallbeassessed.Dur1ngoutagesanduntilpoweroperationisagainrealized,thelastoperatingstackandoffgasmonitoralarmsetpointsshallbeused.
Inallcases,thefollowing relationships willhold-Foracalendarquarter:D<1.5mremtotal.bodyrD<5mremforanyorgant-Forthecalendaryear:D<3.0mremtotalbody'-D<10mremforanyorganwhereDtotaldosereceivedduetoliquideffluentreleasesIftheselimitsareexceeded, aspecialreportwillbesubmitted totheNRCidentifying thecause'and proposedcorrective'actions.
"s~>j 3.1.1(Cont'd)Sincemonitorsrespondtonoblegasesonly,monitoralarmpointsaresettoalarmpriortoexceedingthecorrespondingtotalbodydoserates.Theskindoseratelimitisnotusedinsetpointcalculationsbecauseitisneverlimiting.3.1.2StackMonitorSetpointsThedetailedmethodsforestablishingsetpointsshallbecontainedinthestationprocedures.Thesemethodsshallapplythefollowing"general"criteria:(1)RationaleforStackmonitorsettingsisbasedonthegeneralequation:'releaserateactualcorrespondingdoserate,actualreleaseratemax.allowablecorrespondingdoserate,max.allowable~E'X/QE(eM)-Mnax500mr/yrwhere:,yCi/secreleasedrateforeachisotope,iX/Qhighestlandsectorsiteboundary(elevated)dispersionparameter(seeTable3-1)Mi3gammaairdosefactorinunitsofmr/yr/yCi/m(SeeTable4-1)(9)instantaneousreleaseratelimit.max k+i$Ql<<14 3.1.2(Cont'd)(2)Toensurethat10CFR20andTechnicalSpecificationsdoseratelimitsarenotexceeded,thehihialarmsonthestackmonitorsshallbesetlowerthanorequalto(0.9)(Q).Hialarmsmax'hallbesetlowerthanorequalto(0.5)(Q)max(3)Basedontheaboveconservatism,thedose'contributionfromJAFandNMP-2canusuallybeignored.DuringEmergency'lassificationsatJAForNHP-2duetoairborneeffluent,orafteremergencycondenserventreleasesofsignificantproportions,the500mr/yrvaluemaybereducedaccordingly.(4)ToconvertmonitorgrosscountratestopCi/secreleaserates,thefollowinggeneralformulasilallbeapplied:(C-B)KQpCi/secreleaseratewhere:CmonitorgrosscountrateincpsorcpmB~-monitorbackgroundcountrateKstackmonitorefficiencyfactorwithunitsofpCi/sec-cpsorpCi/sec-cpm.(5)MonitorKfactorsshallbedeterminedusingthegeneralformula:KsEi(Q)i(C-8)where:individualradionuclidestackeffluentreleaserateasdeterminedbyisotopicanalysis.Kfactorsmoreconservativethanthosecalculatedbytheabovemethodologymaybeassumed.
Inaddition, iftheselimitsareexceededbyafactoroftwo,calculations shallbemadetodetermine ifthedoselimits-contained in"40CPR190have.beenexceeded.
Doselimits,ascontained in40CFR190aretotalbodyandorgandosesof25mremperyearandathyroiddoseof75mremperyear.
r,'IP 2.3.1(Cont'd)Thesecalculations willincludedosesasaresultofliquidandgaseouspathwaysaswellasdosesfromdirectradiation.
Liquid,gaseousanddirectradiation pathwaydoseswillconsidertheJamesA.Fitzpatrick andNineMilePointUnitIIfacilities aswellasNineMilePointUnitINuclearStation.Inthe'event-thecalculations demonstrate thatthe40CFR190doselimits,asdefinedabove,havebeenexceeded, thenareportshallbepreparedandsubmitted totheCommission within30daysasspecified inSection3.6.15.doftheTechnical Specifications.
~:"'"Section 4.0ofthe'DCMcontainsmoreinformation concerning calculations foranevaluation,of=whether 40CFR190limits.havebeenexceeded.
QtpN@i  


3.1.2(Cont'd)Alternatively,whenstackreleaseratesarenearthelowerlimitofdetection,thefollowinggeneralformulamaybeusedtocalculatekf(Yf')~Hdsfwhere:fstackflowincc/secE-effic1ency1nunitsofcpmcc/pC1orcpscc/pC1Ekcpmcc/bpsorcpscc/gsfromenergycalibrationcurveproduceddur1ngNBStraceablepr1marygascalibrationortransfersourcecalibrationYkb/d(betas/disintegration)orW/d(gammas/d)IFiActivityfractionofnuclide1inthem1xturenuclidecounterkdiscreteenergybetaorgammaemitterpernuc11decounters"secondsThismonitorcal1brationmethodassumesanoblegas.distribut1on-typicalofarecoilreleasemechan1sm.To-ensurethatthecalculatedefficiencyisconservative,betaorgammaemissionswhoseenergyisabovetherangeofcalibrationofthedetectorarenotincludedin"*thecalculation.
==3.0 GASEOUSEFFLUENTS==
pl~SI 3.1.3RecombinerDischarge(OffGas)MonitorSetpoints(1)Thehihialarmpointsshallactivatewithrecombinerdischargeratesequaltoorlessthan500,000pCi/sec.ThisalarmpointmaybesetequaltoorlessthanlCi/secforaperiodoftimenottoexceed60daysprovidedtheoffgastreatmentsystemisinoperation.(2)Theh1alarmpointsshallact1vatewithrecombinerdischargeratesequaltoorlessthan500,000pCi/sec(3)ToconvertmonitormR/hrreadingstopCi/sec,theformulabelowshallbeapplied:(R)(KR)QRpCi/secrecombinerdischargereleaseratewhere:RmR/hrmonitorindicatorKRefficiencyfactorinunitsofpCi/sec/mR/hrdeterminedpr1ortosett1ngmonitoralarmpoints(4)MonitorKRfactorsshallbedeterminedusingthegeneral""'formula:KRwhere:ZQi/R'-individualnoblegasradionucliderecombiner<<;dischargereleaserateasdeterminedbyisotop1canalysisandflowratemon1tor.KRfactorsmoreconservativethanthosecalculatedbytheabovemethodologymaybeassumed.
3.lSetpointDeterminations 3.1.1Bas1sStackgasandoffgasmonitorsetpoints willbeestablished suchthattheinstantaneous releaserateofrad1oactive materials ingaseouseffluents doesnotexceedthe10CFR20limitsforannualreleaserate.Thesetpoints willbeactivated iftheinstantaneous doserateatorbeyondthe(land)s1teboundarywouldexceed500mrem/yrtothewholebodyor3000mrem/yrtotheskinfromthecontinuous releaseofradioactive noblegas1nthegaseouseffluent.
Ilf+~~,cg~).gpg~y'g-.e,+w'~"a~'I 3.1.3(Cont'd)(5)Thesetpointschosenprovideassurancethatthetotalbodyexposuretoanindividualattheexclusionareaboundarywillnotexceedaverysmallfractionofthelimitsof10CFRPart100intheeventthiseffluentisinadvertentlydischargeddirectlytotheenvironmentwithouttreatment(therebyimplementingtherequirementsofGeneralDesignCriteria60and64ofAppendixAto10CFRPart'50).Additionally,thesesetpoints.serveto.limitbuildupoffissionproductactivitywithinthestationsystemswhichwouldresultifhighfuelleakageweretobepermittedoverextendedperiods.3.1.4EmergencyCondenserVentMonitorSetpointThemonitorsetpointwasestablishedbycalculation("Emergency,CondenserVentMonitorAlarmSetpoint",January13,1986,NMPCFileCode816199).Assumingahypotheticalcasewith(1)reactorwateriodineconcentrationshigherthantheTechnicalSpecificationKimit,(2)reactorwaternoblegasconcentrationshigherthanwouldbe'!'~'expectedatTechnicalSpecificationiodinelevels,and(3)leakageofreactorsteamintotheemergencycondensershellat300%ofrated6flow(or1.3x10lbs/hr),thecalculationpredictsanemergency.condenserventmonitorresponseof20mr/hr.Suchareleasewouldresultinlessthan10CFR,20doserate.valuesatthesiteboundary-..-".andbeyondfortypicalemergencycondensercooldownperiods.Sincea20mr/hrmonitorresponsecan,intheory,beachievableonlywhenreactorwateriodinesarehigherthanpermittedbyTechnicalSpecifications,aconservativemonitorsetpointof5mr/hrhasbeenadopted.  
Emergency condenser ventmonitorsetpoints willbeestablished suchthatthereleaserateforradioactive materials ingaseouseffluents donotexceedthe10CFR20limitsforannualreleaserateoverthepro)ected longestperiodofrelease.Monitorsetpoints fromcontinuous releasepointsw111bedetermined onceperquarterundernormalreleaseratecond1tions andwillbebasedontheisotopiccomposition oftheactualreleaseinprogress, oranoffgasisotopicdistribution, oramoreconservative defaultcompos1tion specif1ed inthepertinent procedure.
\lae'1PKg~lqb+~'.~>~'/iLiatgr,'k\t 3.1.5Discussion3.1.5.1StackEffluentMonitoringSystemDescriptionTheNMP-1Stack'EffluentMonitoringSystemconsistsoftwo-subsystems;theRadioactiveGaseousEffluentMonitoringSystem(RAGEHS)andtheoldGeneralElectricStackMonitoringSystem-(OGESHS).Duringnormaloperation,theOGESHSshallbeusedtomonitorstationnoblegaseffluentsandcollectparticulateandiodinesamplesincompliancewithTechnicalSpecification,.requirements.TheRAGEHSisdes1gnedtobepromptlyactivatedfromtheMainControlRoomforuseinhighrangemonitoringduringacc1dentsituationsincompliancewith,NUREG0737.crtter1a.OverallsystemschematicfortheOGESHSandRAGEHSareshownonFigureS-9.AsimplifiedviewofRAGEHSShowingUnit0,1,2,3and4canbefoundonFigureS-8.'''he'AGEHScanprovidecontinuousaccidentmonitor1ngandon-lineisotopicanalysisofNMP-1stackeffluentnoblegasesatLowerLevelsofDetectionlessthanTechnicalSpecificat1onTable4.6.15-2lim1ts..Activitiesaslowas5X10andash1ghas2-X10pCi/ccfornoblegasesaredetectablebythe'system.
Ifthecalculated "setpoint's
aAgplQ,yrIaviwwpa<~4)~'(~l'f~r~ph~l17/N 3.1.5.2StackSampleFlowPath-RAGEHSTheeffluentsampleisobtainedinsidethestackatelevation530'singanisokineticprobewithfourorifices.Thesamplelinethenbendsradiallyoutandbackintothestack;descendsdownthestackandoutofthestackatapproximatelyelevation257';runshorizontally(enclosedinheat-tracing)s'ome270'longtheoffgastunnel;andenterstheRAGEHSlocatedontheTurbineBuilding250'Dilutioncabinet-Unit0)andOffGasBuilding247'Particulate,Iodine,NobleGasstations-Units1-3).IntheDilutioncabinetoftheRAGEHS,thestackgasmaybedilutedduringaccidentsituationsapproximately100-200X(firststage)or10000-40000X(firstandsecondstage)withgaseousnitrogensupplied-':'romanon-siteliquidnitrogenstoragetank(seeFigure8-9).FromUnit0,'thesamplegasentersUni,t1-3ofRAGEMSandflowsthruin-lineparticulateandiodinecartridgesandthenthrueithera6".liter',(low'range)or30cc(highrange)noblegaschamber.ThesamplegasnextflowsbackthruUnit0andtheoffgastunnel;andbackintothestack.
'higherthantheexistingsetpoint, itisnotmandatory thatthesetpointbechanged.Monitorsetpoints foremergency condenser ventmonitorsare'conservatively f1xedat5mr/hrforreasonsdescribed inSections3.1.4and.therefore donotrequire.per1odic recalculations.
4Oga'%ygNl+y",,>h&g'4 3.1.5.3StackSampleFlowPath-OGESHSTheOGESHSsampleisobtainedfromthesamestacksampleprobeastheRAGEHS.Fromtheexitofthestackatelevation'257',thesamplelinerunseastapproximately20'ndthen.verticallyapproximately8'otheOGESHSskid.IntheOGESHS,sampleflowsthruaparticulate/iodinecartridge'ousingandfournoblegasscintillationdetectors(ie,07and08lowrangebetadetectorsand11and12highrangegammadetectors).FromOGESMS,thestacksampleflowsbackintothestackatapproximatelyelevation257'.AllOGESHSdetectoroutputsaremonitoredandrecordedremotelyintheHainControlRoom.AlarmingcapabilitiesareprovidedtoalertOperatorsofhighreleaserateconditionspriortoexceedingTechnicalSpecification3.6.15.b(1)adoseratelimits.Stackparticulateandiodines'amplesareretrievedmanuallyfromthe.OGESHSandanalyzedinthelaboratoryusinggammaspectroscopyat''"'"frequenciesandLLDs'specifiedinTable4.6.15-2oftheTechnicalSpecifications.
Underabnormalsitereleaserateconditions, monitoralarmsetpoints fromcontinuous releasepointswillberecalculated and,ifnecessary, resetatmorefrequentintervals asdeemednecessary byCORMSuperv1sion.
p4\/k'(=Np,He'L4s'e>'-6+~v 3.1.5.4,SamplingFrequency/SampleAnalysisRegardlessofwhichstackmonitoringsubsystemisutilized,radioactivegaseouswastesshallbesampledandanalyzedinaccordancewiththesamplingandanalysisprogramspecifiedinTechnicalSpecificationTable4.6.15-2.-Particulate.samplesare.;,savedandanalyzedforprincipalgammaemitters,grossalpha,Fe-55,Sr-89,Sr.-90atmonthlyintervalsminimally.Thelatterthreeanalysesareperformedoff-sitefromacompositesample.Sample".analysisfrequenciesare.increasedduringelevatedreleaserateconditions,followingstartup,shutdown,andincon]unctionwitheachdrywellpurge.'-'onsistentwithTechnicalSpecificationTable4.6.15-2,stackeffluenttritiumissampledmonthly,duringeachdrywellpurge,andweeklywhenfuelisoffloadeduntilstablereleaseratesaredemonstrated.Samplesareanalyzedoff-site.Linelosscorrectionfactorsareappliedtoallparticulateandiodineresults.Correctionfactorsof2.0and1.5areusedfordata-obtainedfromRAGEHSand.OGESHSrespectively.Thesecorrectionfactorsarebasedonempirical.datafrom-samplingconducted,at-NMP-1in1985(memofrom3.BlastaktoRAGEHSFile,1/6/86,"StackSampleRepresentativenessStudy:RAGEHSvs.In-StackAuxiliaryProbeSamples").  
Inpart1cular, contr1butions frombothJAFand'MP-2andtheEmergency Condenser Ventsshallbeassessed.
Dur1ngoutagesanduntilpoweroperation isagainrealized, thelastoperating stackandoffgasmonitoralarmsetpoints shallbeused.
"s~>j 3.1.1(Cont'd)Sincemonitorsrespondtonoblegasesonly,monitoralarmpointsaresettoalarmpriortoexceeding thecorresponding totalbodydoserates.Theskindoseratelimitisnotusedinsetpointcalculations becauseitisneverlimiting.
3.1.2StackMonitorSetpoints Thedetailedmethodsforestablishing setpoints shallbecontained inthestationprocedures.
Thesemethodsshallapplythefollowing "general"criteria:
(1)Rationale forStackmonitorsettingsisbasedonthegeneralequation:
'releaserateactualcorresponding doserate,actualreleaseratemax.allowable corresponding doserate,max.allowable
~E'X/QE(eM)-Mnax500mr/yrwhere:,yCi/secreleasedrateforeachisotope,iX/Qhighestlandsectorsiteboundary(elevated) dispersion parameter (seeTable3-1)Mi3gammaairdosefactorinunitsofmr/yr/yCi/m (SeeTable4-1)(9)instantaneous releaseratelimit.max k+i$Ql<<14 3.1.2(Cont'd)(2)Toensurethat10CFR20andTechnical Specifications doseratelimitsarenotexceeded, thehihialarmsonthestackmonitorsshallbesetlowerthanorequalto(0.9)(Q).Hialarmsmax'hallbesetlowerthanorequalto(0.5)(Q)max(3)Basedontheaboveconservatism, thedose'contribution fromJAFandNMP-2canusuallybeignored.DuringEmergency
'lassifications atJAForNHP-2duetoairborneeffluent, orafteremergency condenser ventreleasesofsignificant proportions, the500mr/yrvaluemaybereducedaccordingly.
(4)ToconvertmonitorgrosscountratestopCi/secreleaserates,thefollowing generalformulasilallbeapplied:(C-B)KQpCi/secreleaseratewhere:CmonitorgrosscountrateincpsorcpmB~-monitorbackground countrateKstackmonitorefficiency factorwithunitsofpCi/sec-cps orpCi/sec-cpm.
(5)MonitorKfactorsshallbedetermined usingthegeneralformula:KsEi(Q)i(C-8)where:individual radionuclide stackeffluentreleaserateasdetermined byisotopicanalysis.
Kfactorsmoreconservative thanthosecalculated bytheabovemethodology maybeassumed.
 
3.1.2(Cont'd)Alternatively, whenstackreleaseratesarenearthelowerlimitofdetection, thefollowing generalformulamaybeusedtocalculate kf(Yf')~Hdsfwhere:fstackflowincc/secE-effic1ency 1nunitsofcpmcc/pC1orcpscc/pC1Ekcpmcc/bpsorcpscc/gsfromenergycalibration curveproduceddur1ngNBStraceable pr1marygascalibration ortransfersourcecalibration Ykb/d(betas/disintegration) orW/d(gammas/d)
IFiActivityfractionofnuclide1inthem1xturenuclidecounterkdiscreteenergybetaorgammaemitterpernuc11decounters"secondsThismonitorcal1bration methodassumesanoblegas.distribut1on-typicalofarecoilreleasemechan1sm.
To-ensurethatthecalculated efficiency isconservative, betaorgammaemissions whoseenergyisabovetherangeofcalibration ofthedetectorarenotincludedin"*thecalculation.
pl~SI 3.1.3Recombiner Discharge (OffGas)MonitorSetpoints (1)Thehihialarmpointsshallactivatewithrecombiner discharge ratesequaltoorlessthan500,000pCi/sec.ThisalarmpointmaybesetequaltoorlessthanlCi/secforaperiodoftimenottoexceed60daysprovidedtheoffgastreatment systemisinoperation.
(2)Theh1alarmpointsshallact1vatewithrecombiner discharge ratesequaltoorlessthan500,000pCi/sec(3)ToconvertmonitormR/hrreadingstopCi/sec,theformulabelowshallbeapplied:(R)(KR)QRpCi/secrecombiner discharge releaseratewhere:RmR/hrmonitorindicator KRefficiency factorinunitsofpCi/sec/mR/hr determined pr1ortosett1ngmonitoralarmpoints(4)MonitorKRfactorsshallbedetermined usingthegeneral""'formula:
KRwhere:ZQi/R'-individual noblegasradionuclide recombiner
<<;discharge releaserateasdetermined byisotop1canalysisandflowratemon1tor.KRfactorsmoreconservative thanthosecalculated bytheabovemethodology maybeassumed.
Ilf+~~,cg~).gpg~y'g
-.e,+w'~"a~'I 3.1.3(Cont'd)(5)Thesetpoints chosenprovideassurance thatthetotalbodyexposuretoanindividual attheexclusion areaboundarywillnotexceedaverysmallfractionofthelimitsof10CFRPart100intheeventthiseffluentisinadvertently discharged directlytotheenvironment withouttreatment (therebyimplementing therequirements ofGeneralDesignCriteria60and64ofAppendixAto10CFRPart'50).Additionally, thesesetpoints.serve to.limitbuildupoffissionproductactivitywithinthestationsystemswhichwouldresultifhighfuelleakageweretobepermitted overextendedperiods.3.1.4Emergency Condenser VentMonitorSetpointThemonitorsetpointwasestablished bycalculation
("Emergency
,Condenser VentMonitorAlarmSetpoint",
January13,1986,NMPCFileCode816199).Assumingahypothetical casewith(1)reactorwateriodineconcentrations higherthantheTechnical Specification Kimit,(2)reactorwaternoblegasconcentrations higherthanwouldbe'!'~'expected atTechnical Specificationiodine levels,and(3)leakageofreactorsteamintotheemergency condenser shellat300%ofrated6flow(or1.3x10lbs/hr),thecalculation predictsanemergency
.condenser ventmonitorresponseof20mr/hr.Suchareleasewouldresultinlessthan10CFR,20doserate.valuesatthesiteboundary-..-".andbeyondfortypicalemergency condenser cooldownperiods.Sincea20mr/hrmonitorresponsecan,intheory,beachievable onlywhenreactorwateriodinesarehigherthanpermitted byTechnical Specifications, aconservative monitorsetpointof5mr/hrhasbeenadopted.  
\lae'1PKg~lqb+~'.~>
~'/iLiatgr,'k\t 3.1.5Discussion 3.1.5.1StackEffluentMonitoring SystemDescription TheNMP-1Stack'Effluent Monitoring Systemconsistsoftwo-subsystems; theRadioactive GaseousEffluentMonitoring System(RAGEHS)andtheoldGeneralElectricStackMonitoring System-(OGESHS).
Duringnormaloperation, theOGESHSshallbeusedtomonitorstationnoblegaseffluents andcollectparticulate andiodinesamplesincompliance withTechnical Specification
,.requirements.
TheRAGEHSisdes1gnedtobepromptlyactivated fromtheMainControlRoomforuseinhighrangemonitoring duringacc1dentsituations incompliance with,NUREG 0737.crtter1a.
Overallsystemschematic fortheOGESHSandRAGEHSareshownonFigureS-9.Asimplified viewofRAGEHSShowingUnit0,1,2,3and4canbefoundonFigureS-8.'''he'AGEHS canprovidecontinuous accidentmonitor1ng andon-lineisotopicanalysisofNMP-1stackeffluentnoblegasesatLowerLevelsofDetection lessthanTechnical Specificat1on Table4.6.15-2lim1ts..Activities aslowas5X10andash1ghas2-X10pCi/ccfornoblegasesaredetectable bythe'system.
aAgplQ,yrIaviwwpa<~4)~'(~l'f~r~ph~l17/N 3.1.5.2StackSampleFlowPath-RAGEHSTheeffluentsampleisobtainedinsidethestackatelevation 530'singanisokinetic probewithfourorifices.
Thesamplelinethenbendsradiallyoutandbackintothestack;descendsdownthestackandoutofthestackatapproximately elevation 257';runshorizontally (enclosed inheat-tracing) s'ome270'longtheoffgastunnel;andenterstheRAGEHSlocatedontheTurbineBuilding250'Dilution cabinet-Unit0)andOffGasBuilding247'Particulate, Iodine,NobleGasstations-Units1-3).IntheDilutioncabinetoftheRAGEHS,thestackgasmaybedilutedduringaccidentsituations approximately 100-200X(firststage)or10000-40000 X(firstandsecondstage)withgaseousnitrogensupplied-':'romanon-siteliquidnitrogenstoragetank(seeFigure8-9).FromUnit0,'thesamplegasentersUni,t1-3ofRAGEMSandflowsthruin-lineparticulate andiodinecartridges andthenthrueithera6".liter',(low'range) or30cc(highrange)noblegaschamber.ThesamplegasnextflowsbackthruUnit0andtheoffgastunnel;andbackintothestack.
4Oga'%ygNl+y",,>h&g'4 3.1.5.3StackSampleFlowPath-OGESHSTheOGESHSsampleisobtainedfromthesamestacksampleprobeastheRAGEHS.Fromtheexitofthestackatelevation'257',
thesamplelinerunseastapproximately 20'ndthen.vertically approximately 8'otheOGESHSskid.IntheOGESHS,sampleflowsthruaparticulate/iodine cartridge'ousing andfournoblegasscintillation detectors (ie,07and08lowrangebetadetectors and11and12highrangegammadetectors).
FromOGESMS,thestacksampleflowsbackintothestackatapproximately elevation 257'.AllOGESHSdetectoroutputsaremonitored andrecordedremotelyintheHainControlRoom.Alarmingcapabilities areprovidedtoalertOperators ofhighreleaserateconditions priortoexceeding Technical Specification 3.6.15.b(1)adoseratelimits.Stackparticulate andiodines'amplesareretrieved manuallyfromthe.OGESHSandanalyzedinthelaboratory usinggammaspectroscopy at''"'"frequencies andLLDs'specified inTable4.6.15-2oftheTechnical Specifications.
p4\/k'(=Np,He'L4s'e>'-6+~v 3.1.5.4,SamplingFrequency/Sample AnalysisRegardless ofwhichstackmonitoring subsystem isutilized, radioactive gaseouswastesshallbesampledandanalyzedinaccordance withthesamplingandanalysisprogramspecified inTechnical Specification Table4.6.15-2.-
Particulate.
samplesare.;,savedandanalyzedforprincipal gammaemitters, grossalpha,Fe-55,Sr-89,Sr.-90atmonthlyintervals minimally.
Thelatterthreeanalysesareperformed off-sitefromacomposite sample.Sample".analysis frequencies are.increased duringelevatedreleaserateconditions, following startup,shutdown,and incon]unction witheach drywellpurge.'-'onsistent withTechnical Specification Table4.6.15-2, stackeffluenttritiumissampledmonthly,duringeachdrywellpurge,andweeklywhenfuelisoffloadeduntilstablereleaseratesaredemonstrated.
Samplesareanalyzedoff-site.
Linelosscorrection factorsareappliedtoallparticulate andiodineresults.Correction factorsof2.0and1.5areusedfordata-obtained fromRAGEHSand.OGESHS respectively.
Thesecorrection factorsarebasedonempirical.
datafrom-sampling conducted, at-NMP-1in1985(memofrom3.BlastaktoRAGEHSFile,1/6/86,"StackSampleRepresentativeness Study:RAGEHSvs.In-StackAuxiliary ProbeSamples").  
<<v~ft~t1l~'W~"
<<v~ft~t1l~'W~"
3.1.5.5I-133EstimatesMonthly,thestackeffluent.shallbesampledforiodinesovera24hourperiodandtheI-135/I-131andtheI-133/I-131ratioscalculated.TheseratiosshallbeusedtocalculateI-133,I-135releaseforlongeracquisitionsamples-collectedduringthemonth.Additionally,-theI-135/I-131andI-133/I-131ratiosshouldalsobe5determinedafterasignificantchangeintheratioissuspected(eg,plantstatuschangesfromprolongedshutdowntopoweroperationorfueldamagehasoccurred).3.1.5.6GaseousRadwasteTreatmentSystemOperationTechnicalSpecification3.6.16.brequiresthatthegaseousradwastetreatmentsystemshallbeoperableandshallbeusedtoreduceradioactivematerialsingaseouswastepriortotheirdischargeasnecessarytomeettherequirementsofTechnicalSpecification3.6.15.b.ToensureTechnicalSpecification3.6.15.blimitsarenotexceeded,andtoconfirmproperradwastetreatmentsystemoperationas'applicable,cumulativedosecontributionsforthecurrentcalendarquarterand'current-calendar."yearshallbedeterminedmonthlyinaccordancewithsection3.2ofthismanual.Initialdosecalculationsshallincorporatethefollowingassumptionswithregardtoreleaseratesofnon-gammaemittingradionuclidessubsequentlyanalyzedoff-site:  
3.1.5.5I-133Estimates Monthly,thestackeffluent.shallbesampledforiodinesovera24hourperiodandtheI-135/I-131 andtheI-133/I-131 ratioscalculated.
/t1"~=1B~'IQ 3.1.5.6(Cont'd)a)H-3releaserate)4uCi/secb)Sr-89releaserate)4xCs-137releaseratec)Sr-90releaserate)0.5xCs-137releaserated)Fe-55releaserate)1xCo-60releaserateAssumedreleaseratesrepresentconservativeestimatesderivedfromanalysisofhistoricaldatafromeffluentreleasesandprocesswastestreams(SeeNMP34023,C.MaretoJ.Blasiak,April29,1988,"DoseEstimatesforBeta-EmittingIsotopes".).FollowingreceiptofVoff-siteH-3,Sr-89,Sr-90,Fe-55analysisinformation,doseestimatesshallberevisedusingactualradionuclideconcentrations.3.2DoseandDoseRateDeterminationsInaccordancewithspecifications4.6.15.b.(2)and4.6.15.b.(3),doseanddoseratedeterminationswillbemademonthlyinordertodetermine:(1)TotalbodydoseratesandgammaairdosesatthemaximumX/Qlandsector'siteboundaryinterfaceandbeyond.(2)SkindoseratesandbetaairdosesatthemaximumX/Qlandsectorsiteboundaryinterfaceandbeyond.(3)ThecriticalorgandoseanddoserateatthemaximumX/Qlandsectorsiteboundaryinterfaceandatacriticalreceptorlocationbeyondthesiteboundary.~
Theseratiosshallbeusedtocalculate I-133,I-135releaseforlongeracquisition samples-collected duringthemonth.Additionally,-the I-135/I-131 andI-133/I-131 ratiosshouldalsobe5determined afterasignificant changeintheratioissuspected (eg,plantstatuschangesfromprolonged shutdowntopoweroperation orfueldamagehasoccurred).
f',4*4h 3.2(Cont'd)Eitheraveragemeteorologicaldata(ie,maximumfiveyearannualaverageX/QandD/Qvaluesinthecaseofelevatedreleasesor1985annualaverageX/QandD/Qvalues,inthecaseofgroundlevelreleases)orrealtimemeteorologicaldatashallbeutilizedfordoseanddoseratecalculations.Whereaveragemeteorologicaldataisassumed,doseanddoseratesduetonoblegasesatlocationsbeyondthe'iteboundarywillbelowerthanequivalentsiteboundarydoseanddoserates.Therefore,undertheseconditions,calculationsofnoblegasdoseanddoseratesbeyondthemaximumX/Qlandsectorsiteboundarylocationscanbeneglected-Thefrequencyofdoseratecalculationswillbeupgradedwhenelevatedreleaserateconditionsspecifiedinsubsequentsections3.2.1.1and3.2.1.2arerealized.EmergencycondenserventreleasecontributionstothemonthlydoseanddoseratedeterminationswillbeconsideredonlywhentheemergencycondenserreturnisolationvalveshavebeenopenedforreactorcooldownorifEmergencyCondensertubeleaksdevelopwithorwithoutthesystem'sreturnisolationvalveopened.Withouttubeleakageoropeningof,thereturnisolationvalves,releasesfromthissystemarenegligibleandthecorrespondingdosecontributionsdonothavetobeincluded.  
3.1.5.6GaseousRadwasteTreatment SystemOperation Technical Specification 3.6.16.brequiresthatthegaseousradwastetreatment systemshallbeoperableandshallbeusedtoreduceradioactive materials ingaseouswastepriortotheirdischarge asnecessary tomeettherequirements ofTechnical Specification 3.6.15.b.
ToensureTechnical Specification 3.6.15.blimitsarenotexceeded, andtoconfirmproperradwastetreatment systemoperation as'applicable, cumulative dosecontributions forthecurrentcalendarquarterand'current-calendar."year shallbedetermined monthlyinaccordance withsection3.2ofthismanual.Initialdosecalculations shallincorporate thefollowing assumptions withregardtoreleaseratesofnon-gamma emittingradionuclides subsequently analyzedoff-site:  
/t1"~=1B~'IQ 3.1.5.6(Cont'd)a)H-3releaserate)4uCi/secb)Sr-89releaserate)4xCs-137releaseratec)Sr-90releaserate)0.5xCs-137releaserated)Fe-55releaserate)1xCo-60releaserateAssumedreleaseratesrepresent conservative estimates derivedfromanalysisofhistorical datafromeffluentreleasesandprocesswastestreams(SeeNMP34023,C.MaretoJ.Blasiak,April29,1988,"DoseEstimates forBeta-Emitting Isotopes".).
Following receiptofVoff-siteH-3,Sr-89,Sr-90,Fe-55analysisinformation, doseestimates shallberevisedusingactualradionuclide concentrations.
3.2DoseandDoseRateDeterminations Inaccordance withspecifications 4.6.15.b.(2) and4.6.15.b.(3),
doseanddoseratedeterminations willbemademonthlyinordertodetermine:
(1)TotalbodydoseratesandgammaairdosesatthemaximumX/Qlandsector'siteboundaryinterface andbeyond.(2)SkindoseratesandbetaairdosesatthemaximumX/Qlandsectorsiteboundaryinterface andbeyond.(3)ThecriticalorgandoseanddoserateatthemaximumX/Qlandsectorsiteboundaryinterface andatacriticalreceptorlocationbeyondthesiteboundary.~
f',4*4h 3.2(Cont'd)Eitheraveragemeteorological data(ie,maximumfiveyearannualaverageX/QandD/Qvaluesinthecaseofelevatedreleasesor1985annualaverageX/QandD/Qvalues,inthecaseofgroundlevelreleases) orrealtimemeteorological datashallbeutilizedfordoseanddoseratecalculations.
Whereaveragemeteorological dataisassumed,doseanddoseratesduetonoblegasesatlocations beyondthe'iteboundarywillbelowerthanequivalent siteboundarydoseanddoserates.Therefore, undertheseconditions, calculations ofnoblegasdoseanddoseratesbeyondthemaximumX/Qlandsectorsiteboundarylocations canbeneglected-Thefrequency ofdoseratecalculations willbeupgradedwhenelevatedreleaserateconditions specified insubsequent sections3.2.1.1and3.2.1.2arerealized.
Emergency condenser ventreleasecontributions tothemonthlydoseanddoseratedeterminations willbeconsidered onlywhentheemergency condenser returnisolation valveshavebeenopenedforreactorcooldownorifEmergency Condenser tubeleaksdevelopwithorwithoutthesystem'sreturnisolation valveopened.Withouttubeleakageoropeningof,thereturnisolation valves,releasesfromthissystemarenegligible andthecorresponding dosecontributions donothavetobeincluded.  
~i'F1(Ik$C>>c!
~i'F1(Ik$C>>c!
3.2(Cont'd)'henreleasesfromtheemergencycondenserhaveoccurred,doseanddo'seratedeterminationsshallbeperformedusingmethodologyin3.2.1and3.2.2.Furthermore,enviromentalsamplingmayalsobeinitiatedtorefineanyactualcontributiontodoses.SeeSection3.4.Criticalorgandosesanddoseratesmaybeconservativelycalculatedbyassumingtheexistenceofaso-called"moving"criticalreceptor.Atthis"moving"criticalreceptorlocation,itisassumedthatall'"*'pa'thways"are.applicableandthehighestX/Qand/orD/QvalueforractualpathwaysasnotedinTable3-1areineffect.Aperson'sdoseatthe"moving"criticalreceptorlocationsisequaltothesamedosethatpersonwouldreceiveiftheyweresimultaneouslysubjectedtothehighestpathwaydoseateachcriticalreceptoridentifiedforeachpathway.Ifdoseordoseratescalculated,usingtheassumptionsnotedabove,reachTechnicalSpecificationlimits,actualpathwayswillbeevaluated,anddose/doseratesshallbecalculatedatseparatecriticalreceptorlocationsandcomparedwithapplicablelimits.3.2.1DoseRateNotallpathwaysneedbeconsideredindoseanddoseratecalculationsateachcriticalreceptorlocation.Forexample,when*--"'"calcul'atinglandsectorsite.boundarydosesanddoseratesforparticulates,iodinesandtritium,onlythegrounddepositionandinhalationpathwaysapply.  
3.2(Cont'd)'henreleasesfromtheemergency condenser haveoccurred, doseanddo'seratedeterminations shallbeperformed usingmethodology in3.2.1and3.2.2.Furthermore, enviromental samplingmayalsobeinitiated torefineanyactualcontribution todoses.SeeSection3.4.Criticalorgandosesanddoseratesmaybeconservatively calculated byassumingtheexistence ofaso-called "moving"criticalreceptor.
/jism 3.2.1.1NobleGasesIn'accordancewiththe-provisions.of10CFR20thedoseratesfromnoblegasreleasefromthesitetounrestrictedareasaretobelimitedto500mrem/yrtotheskin.Doseratecalculationwillbeperformedmonthly,orwhentheHiHistackmonitoralarmpointisreached,usingthefollowingequations:Fortotalbodydoserates(inmr/yr):DR+~3.17x10f[Mi(X/Q)Qi/]Forskindoserates(inmRad/yr):DR/+a3.17x10~[Ni(X/Q)Qi/sec]+DR+where:-8Mi,Ni,X/Q,Qi,.3.17x10areasdefinedinsection3.2.2.13.2.1.2Tritium,ZodinesandParticulates(1)Thedoserateinunrestrictedareas'romthe'releaseoftritium,iodine-131,iodine-133andallradionuclidesinparticulateformwithhalflivesgreaterthan8daysislimitedto1500mrem/yeartoanyorgan.  
Atthis"moving"criticalreceptorlocation, itisassumedthatall'"*'pa'thways "are.applicable andthehighestX/Qand/orD/QvalueforractualpathwaysasnotedinTable3-1areineffect.Aperson'sdoseatthe"moving"criticalreceptorlocations isequaltothesamedosethatpersonwouldreceiveiftheyweresimultaneously subjected tothehighestpathwaydoseateachcriticalreceptoridentified foreachpathway.Ifdoseordoseratescalculated, usingtheassumptions notedabove,reachTechnical Specification limits,actualpathwayswillbeevaluated, anddose/dose ratesshallbecalculated atseparatecriticalreceptorlocations andcomparedwithapplicable limits.3.2.1DoseRateNotallpathwaysneedbeconsidered indoseanddoseratecalculations ateachcriticalreceptorlocation.
~!',1'I 3.2.1.2(Cont'd)(2)Enordertoensurethat,.the1500mrem/yeardoseratelimitisnotexceeded,particulate,iodineandtritiumoffsitedoseratecalculationsshallbeperformedmonthlyandwheneverparticulateandiodinereleaseratesexceed0.3pCi/secusingtheequationgiveninSection3.2.2.2withQexpressediniiCi/sec.Whenthe"releaserateexceeds0.3uCi/sec,thedoserateassessmentshallalsoincludeJAFandNMP-2contribution.(3)Theuseofthe0.3vCi/secreleaseratethresholdtoperform""''""doseratecalculationsis)ustifiedasfollows:P(a)The1500mrem/yrorgandoseratelimitcorrespondstoaminimumreleaseratelimitof0.30nCi/seccalculatedusingtheequation:1500(Q/sec)x(Ri)W))where:1500siteboundarydoseratelimitinmrem/year(Ri)W))"themaximumcurie-to-dose'conversionfactorequalto4900mrem-sec/uCi-yrforSr-90,childboneatthe"moving"criticalreceptorlocationbeyondthesiteboundary.
Forexample,when*--"'"calcul'ating landsectorsite.boundarydosesanddoseratesforparticulates, iodinesandtritium,onlythegrounddeposition andinhalation pathwaysapply.  
Tp(\pl 3.2.1.2(Cont'd)(b)Theuseof0.3iiCi/secreleaseratethresholdandthe4900mrem-sec/vCi~rcurie-toroseconversionfactorisconservativesincecurie-toroseconversionfactorsforotherisotopeslikelytobepresentaresignificantly.lower.Forexample,I-131hasthesecondhighestcurie-to-dosefactorequalto465mrem-sec/uCi-yrfortheinfantthyroid.Thiscorrespondstoareleaseratelimitofapproximately3nCi/sec.3.2.2DoseCalculationswillbeperformedmonthlyataminimum,todemonstratethatdosesresultingfromthereleaseofnoblegases,tritium,I-131,I-133andparticulateswithhalflivesgreaterthan8daysarewithinthelimitsspecifiedin10CFR50,AppendixI.Theselimitsare:NobleGasAirDose5mrgamma/calendarquarter10mradbeta/calendarquarter10mrgamma/calendaryear'0mradbeta/calendaryearRadioiodines,Tritium&Particulates7.5mremtoanyorgan/calendarquarter"'15'mrem-toanyorgan/calendar.year 4NQSiI<<4.4I 3.2.2.1NobleGasAirDose-''-The-air'doseatthecritical.receptorduetonoblegasreleasesisdeterminedasfollows:ForgammaradfationDg3.17x107MiX/QForbetaradiationD<~3.17x10E'iX/QQiwhereMairgammadosefactorin(mr/yearperuCi/m)for3i.eachisotopei(Table4-1)3N~airbetadosefactor(mrad/yearperuCi/m)foreachisotopei(Table4-1)X/Qtherelativeplumeconcentration(inunitsofsec/m)atthelandsectorsiteboundaryor3beyond.Eitheraveragemeteorologicaldata(Table3-1orAppendixC),orrealtimevaluesmaybeassumed."Elevated"X/Qvaluesareusedforstackreleases;"Ground"X/Qvaluesareusedfor;EmergencyCondenserVentreleases.Q~thetotalquantityofisotopeireleasedduring.theperiod,(pCi)-83.17x10-~theinverseofthenumberofsecondsinayear.
/jism 3.2.1.1NobleGasesIn'accordance withthe-provisions.of 10CFR20thedoseratesfromnoblegasreleasefromthesitetounrestricted areasaretobelimitedto500mrem/yrtotheskin.Doseratecalculation willbeperformed monthly,orwhentheHiHistackmonitoralarmpointisreached,usingthefollowing equations:
4V'fe 3.2.2.2Radioiodine,Tritium&ParticulatesThedosestoanindividualfromI-131,I-133,tritium,andparticulateswithhalflivesgreaterthan8dayswillbecalculatedasfollows:-8Dose3.17x10R~EiRi~akW~QiWhereWJdispersionparametereitherX/Q(sec/m)orD/Q3(1/m)dependingonpathwayandreceptorlocation2assumed.Eitheraveragemeteorologicaldata(Table3-1,orAppendixC)orrealtimevaluesmaybeassumed."Elevated"Wvaluesareusedforstackreleases;"Ground"WvaluesareusedforEmergencyCondenserVentreleases.thetotalquanityofisotopeireleasedduringtheperiod,(uCi)izaak3':17;x10thedosefactorforeachisotopei,pathwayj,agegroupa,andorgank(Table4-2,through4-20)~theinverseofthenumberofsecondsinayearTheRvaluescontained.in'Tables,4-2,through4-20werecalculatedusingthemethodologydefinedinNUREG-0133,andRegulatoryGuide1.109,Revision1.  
Fortotalbodydoserates(inmr/yr):DR+~3.17x10f[Mi(X/Q)Qi/
-~4W 3.2.2.3AccumulatingDosesDoseswillbecalculatedmonthly,ataminimum,forgammaairandbetaair,theidentifiedcriticalorgan,andagegroup.Resultswillbesummedforeachcalendarquarterandyear.Ithasbeenhistoricallydemonstratedthatthecriticalpathwayisusuallythegrass-cow-milkpathwayandthecriticalorganis,the.,,infant',sthyroid.Forthisreason,monthlyinfantthyroiddoseestimateswillnormallybemadepriortoreceiptofallanalysisdata(i.e.,strontiumandtritium).Thecriticaldosesarebasedonthe,followingpathways:noblegasplumeairdosegroundplanedose(deposition)inhalationdosecow'smilkdosegoat'smilkdosemeatconsumptiondosevegetation(foodcrops)doseThequarterlyandannualresultsshallbecomparedtothelimitslistedin'.paragraph3.2.2.Ifthelimitsareexceeded,specialreports,asrequiredbySection.6.9.3of-theTechnicalSpecification,shallbesubmitted.
]Forskindoserates(inmRad/yr):
kl~A~4~gt4p~'J-4I''fi 3.3CriticalReceptorsInaccordancewiththeprovisionsof10CFR20and10CFR50,AppendixI,thecriticalreceptorshavebeenidentifiedandarecontainedinTable3-1..."For...noblegas:doses,one.oftwocriticalreceptorlocationswillbeassumed.WhenmaximumfiveyearaverageannualX/Qvaluesareused,thecriticalreceptoristhemaximumX/Qlandsectorsiteboundary1interface.WhenrealtimemeteorologicalX/Qvaluesareused,thecriticalreceptormayeitherbethemaximumX/Qlandsectorsiteboundarylocation,orthedownwindlocationofgreatestX/Qresidence(e.g.,1.5mileseast),whicheverishigher.ForI-133,I-131,tritiumandparticulateradionuclideswithhalflifegreaterthaneightdays,thecriticalpathwaysaremilk(cowandgoat>,meat,vegetation,inhalationanddirectradiation(groundplane)asaresultofgrounddeposition.ThecowmilkandgoatmilkpathwaywillbebasedonthegreatestD/Q~...*'ilk,.cowandmilkgoatlocationasdeterminedbytechnicalspecification'.3.6.22.',.The'inhalation'dosepathway,will.bebased-onthegreatestX/Qresidenceasdeterminedbytechnicalspecification3.6.22sincethislocationwouldhavethegreatestpotentialoccupancytime.ThegroundplanedosepathwaywillbecalculatedasthegreatestD/Qresidencebecauseofthegreatestpotentialoccupancytime.-38" lp4l\Ci$il+i' 3.3(Cont'd)Forthemeatconsumptiondosepathway,thecriticalreceptoristhegreatestD/Qmeatanimallocation.Thislocationhasbeendeterminedinconjunctionwiththelandusecensus(technicalspecification3.6.22)andissubjecttochange.Thevegetation(foodcrop)doseisbasedonthegreatest-D/Qgardenlocationfromwhichsamplesare.taken.Thislocationalso.maybemodified:asaresult.of.vegetationsamplingsurveys.3.4RefinementofOffsiteDosesResultingfromEmergencyCondenserVentReleasesThedosesresultingfromtheoperationoftheemergencycondensersandcalculatedinaccordancewith3.2.2mayberefinedusingdatafromactualenviromentalsamples.Grounddepositionsampleswillbeobtainedfromanareaorareasofmaximumprojecteddeposition.Theseareasareanticipatedtobeat<,<or..near.thesiteboundaryandnearprojectedplumecenterline.UsingthemethodologyfoundinRegulatoryGuide1.109,thedosewillbecalculatedtothemaximumexposedindividual.Thisdosewillthenbecomparedtothedosecalculatedinaccordancewith3.2.2.Thecomparisonwillresult,inanadjustmentfactoroflessthanor.greaterthanonewhichwillbeusedtoadjust"the'otherdosesfromotherpathways.  
DR/+a3.17x10~[Ni(X/Q)Qi/sec]
+jl..LS 3.4(Cont'd)Otherenvironmentalsamplesmayalsobecollectedandtheresultantcalculateddosestothemaximumexposedindividualcomparedtothedosecalculatedper3.2.2.Otherenvironmentalsamplemediamayincludemilk,vegetation(suchasgardenbroadleafvegetables),etc.'"."Theadjustment:factors.from.these.pathwaysmaybeappliedtothedosescalculatedper3;2.2onapathwaybypathwaybasisorseveralpathwayadjustmentfactorsmaybeaveragedandusedtoadjustcalculateddoses.DosescalculatedfromactualenvironmentalsamplemediawillbebasedonthemethodologypresentedinRegulatoryGuide1.109.Theregulatoryguideequationsmaybeslightlymodifiedtoaccountforshortintervalsoftime(lessthanoneyear)ormodifiedforsimplicitypurposesbydeletingdecayfactors.Deletionofdecayfactorswouldyieldmoreconservativeresults.  
+DR+where:-8Mi,Ni,X/Q,Qi,.3.17x10areasdefinedinsection3.2.2.13.2.1.2Tritium,ZodinesandParticulates (1)Thedoserateinunrestricted areas'rom the'releaseoftritium,iodine-131, iodine-133 andallradionuclides inparticulate formwithhalflivesgreaterthan8daysislimitedto1500mrem/year toanyorgan.  
~~~'a 4.040CFR190REQUIREMENTSThe"UraniumFuelCycle"isdefinedin40CFRPart190.02(b)asfollows:-"Uraniumfuelcycle'eanstheoperationsofmillingofuraniumore,chemical-conversionofuranium,isotopic-enrichmentofuranium,fabricationofuraniumfuel,generationofelectricitybyalight-water-coolednuclearpowerplantusinguraniumfuel,andreprocessingofspenturaniumfuel,totheextentthatthesedirectlysupporttheproductionofelectrical'owerforpublicuseutilizingnuclearenergy,butexcludesminingoperations,operations.atwastedisposalsites,transportationofanyradioactivematerialinsupport.oftheseoperations,andthereuseofrecoverednon-uraniumspecialrnuclearandby-productmaterialsfromthecycle."Section3.6.15.doftheTechnicalSpecificationsrequiresthatwhen~'.thecalculateddosesassociatedwiththeeffluentreleasesexceedtwicethelimitsofsections3.6.15.a.(2)(b),3.6.15.b.(2)(b)and3.6.15.b.(3)(b),thencalculationsshallbemadeincludingdirectradiationcontributionsfromthereactorunitsand.outsidestoragetanks(asapplicable)-todeterminewhetherthe40CFR190dose-limitshavebeenexceeded.  
~!',1'I 3.2.1.2(Cont'd)(2)Enordertoensurethat,.the 1500mrem/year doseratelimitisnotexceeded, particulate, iodineandtritiumoffsitedoseratecalculations shallbeperformed monthlyandwheneverparticulate andiodinereleaseratesexceed0.3pCi/secusingtheequationgiveninSection3.2.2.2withQexpressed iniiCi/sec.
~~~"0Eff,ffE'~~IfkEI~'kI'II~PIEQ',WEE,Wt~IFEIFJIfJj4I'00fIJI~~FfFQf 4.0(Cont'd)Ifsuchisthecase,NiagaraMohawkshallsubmitaSpecialReporttotheNRCandlimitsubsequentreleasessuchthat.thedosecommitmenttoarealindividualfromalluraniumfuelcyclesourcesislimitedto<'25mremtothe'totalbodyor-anyorgan--(except-the,.thyroid,'which'islimitedto<..75mrem)overthecalendaryear.Thisreportistodemonstratethatradiationexposurestoallrealindividualsfromalluraniumfuelcyclesources(includingallliquidandgaseouseffluentpathwaysanddirectradiation)arelessthanthelimitsin40CFRPart190.Ifreleasesthatresultindosesexceedingthe40CFR190limitshaveoccurred,thenavariancefromtheNRCtopermitsuchreleaseswillberequestedandifpossible,actionwillbetakentoreducesubsequentreleases.""'"The"reporttotheNRCshallcontain:1)Identificationofalluraniumfuelcyclefacilitiesor'perationswithin5milesofthenuclearpowerreactorunitsatthesitethatcontributeto,the-annualdoseofthemaximumexposedmemberofthepublic.2)Identificationofthemaximumexposedmemberofthepublicandadeterminationofthetotalannualdosetothispersonfromexistingpathwaysandsourcesofradioactiveeffluentsanddirectradiation.<<42-J'-~4~>f4p 4.0(Cont'd)Themaximumtotalbodyandorgandosesresultingfromradioactive-materialinliquideffluentsfromNineMilePointUnit1will.besummedwiththemaximumdosesresultingfromthereleasesofnoblegases,radioiodines,andparticulatesfortheothercalendarquarters~>>~--(as.applicable)...and,from.thecalendar.,quarterin,whichtwicethe..limitwasexceeded.Thedirectdosecomponentswillbedeterminedbyeithercalculationoractualmeasurement.ActualmeasurementswillutilizeenvironmentalTLDdosimetry.Calculatedmeasurementswillutilizeengineeringcalculationstodetermineaprojecteddirectdosecomponent.Zntheeventcalculationsareused,themethodologywillbedetailedasrequiredinSection6.9.1.eoftheTechnicalSpecifications.ThedosesfromNineMilePointUnit1willbeaddedtothedosestothemaximumexposedindividualthatarecontributedfromotheruraniumfuelcycleoperationswithin5milesofthesite.Forthepurposeofcalculatingdoses,'heresultsoftheRadiologicalEnviromentalMonitoringProgrammaybeincludedforprovidingmorerefinedestimatesofdosesto.areal.maximumexposedindividual;..Estimateddoses,ascalculatedfromstationeffluents,maybereplacedbydosescalculatedfromactualenviromentalsampleresults.  
Whenthe"releaserateexceeds0.3uCi/sec,thedoserateassessment shallalsoincludeJAFandNMP-2contribution.
~e~~eeee~~~eeeIeeeDEeeeeeeeee EvaluationofDosesFromLiquidEffluentsFortheevaluationofdosestorealmembersofthepublicfromliquideffluents,thefishconsumptionandshorelinesedimentgrounddosewillbeconsidered.Sincethedosesfromotheraquaticpathwaysareinsignificant,fi'sh'onsumption'and"shoreline'ediment>>aretheonly'wopathwaysthatwill-beconsidered.Thedoseassociatedwith,fishconsumptionmaybecalculatedusingeffluentdataandRegulatoryGuide1.109methodologyorbycalculatingadosetomanbasedonactualfishsampleanalysisdata.Thedoseassociatedwithshorelinesedimentisbasedontheassumptionthattheshorelinewouldbeutilizedasarecreationalarea.ThisdosemaybederivedfromliquideffluentdataandRegulatoryGuide1.109methodologyorfromactualshorelinesedimentsampleanalysisdata.EquationsusedtoevaluatedosesfromactualfishandshorelinesedimentsamplesarebasedonRegulatoryGuide1.109methodology..Because.ofthesamplemediumtypeandthehalf-livesoftheradionuclideshistoricallyobserved,thedecaycorrectedportionsoftheequationsaredeleted.Thisdoesnotreducetheconservatismofthecalculateddosesbutincreasesthesimplicityfromanevaluationpointofview.Thedosefromfishsamplemediaiscalculatedas:(1)Rwb~Fi[Cifxux1000xDiwbxf]Where:~Thetotaldosetothewholebodyofanadultinmremperyear.
(3)Theuseofthe0.3vCi/secreleaseratethreshold toperform""''""doseratecalculations is)ustified asfollows:P(a)The1500mrem/yrorgandoseratelimitcorresponds toaminimumreleaseratelimitof0.30nCi/seccalculated usingtheequation:
A<<+t%eA (Cont'd)Cif~TheconcentrationofradionuclideiinfishsamplesinpCi/gram.~Theconsumptionrateoffishforanadult(21kgperyear).1000~Gramsperkilogram'Diwb~Thedosefactorforradionuclide::iforthewholebodyofanadult(R.G.1.109,TableE-11).~Thefractionalportionoftheyearoverwhichthedoseisapplicable.(2)RlWhere:~~i[Cifxyx1000xDilx~Thetotaldosetotheliverofanadult(maximumexposedorgan)inmremperyear.Cif=TheconcentrationofradionuclideiinfishsamplesinpCi/gram.~Theconsumptionrateoffishforanadult(21kgperyear).1000~GramsperkilogramDil~Thedosefactorforradionuclideifortheliverofanadult(R.G.1.109,TableE-ll)~Thefractionalportionoftheyearoverwhichthedoseisapplicable.Thedosefromshorelinesedimentsamplemediaiscalculatedas:Where:-E[Ci,xllx-40,000x0.3xDiwbxf]and~g[Cisxyx40,000x0.3xDiskxf]~Thetotaldosetothewholebodyofateenageroradult(maximumexposedagegroup),inmremperyear.Rsk~Thetotaldosetotheskinofateenageroradult(maximumexposedagegroup)inmremperyear.Cis~The-concentrationofradionuclideiinshorelinesedimentinpci/gram.
1500(Q/sec)x(Ri)W))where:1500siteboundarydoseratelimitinmrem/year (Ri)W))"themaximumcurie-to-dose'conversion factorequalto4900mrem-sec/uCi-yr forSr-90,childboneatthe"moving"criticalreceptorlocationbeyondthesiteboundary.
4"0AgR)i"I (Cont'd)~Theusagefactor.Thisisassumedas67hoursperyearbyateenageroradult.I40,000~Theproductoftheassumeddensityofshorelinesediment(40kilogrampersquaremetertoadepthof2.5cm)timesthenumberofgramsperkilogram.0.3~Theshorewidthfactorforalake,Diwb=The'dosefactorfor'radionuclideiforthetotal,body(R.G.1.109,TableE-6)Disk~Thedosefactorforradionuclideifortheskin(R.G.1.109,TableE-6)~Thefractionalportionoftheyearoverwhichthedoseisapplicable.NOTE:"'ecauseofthenatureofthereceptorlocationandtheextensivefishingactivityinthearea,thecriticalindividual-maybeateenageroranadult.
Tp(\pl 3.2.1.2(Cont'd)(b)Theuseof0.3iiCi/secreleaseratethreshold andthe4900mrem-sec/vCi~r curie-torose conversion factorisconservative sincecurie-torose conversion factorsforotherisotopeslikelytobepresentaresignificantly
Qb.~iiIh'4*~~~'ial4lhkgtlXfCkingil0~iii\f1E1'h'4gt0tl~iit4 4.2EvaluationofDosesFromGaseousEffluentsFortheevaluationofdosestorealmembersofthepublicfromgaseouseffluents,thepathwayscontainedinsection3.2.2.3oftheODCMwillbeconsidered.Theseincludetheingestion,inhalationand'depositionpathways'.However,anyupdatedfield:datamay.beutilizedthatconcernslocationsofrealindividuals,realtimemeteorologicaldata,locationofcriticalreceptors,etc.Datafromthemostrecentcensusandsamplelocationsurveysshouldbeutilized.Dosesmayalsobecalculatedfromactualenviromentalsamplemedia,asavailable.EnviromentalsamplemediadatasuchasTID,airsample,milksampleandvegetable(foodcrop)sampledatamaybeutilizedinlieuofeffluentcalculationaldata.DosestomemberofthepublicfromthepathwasycontainedinODCMsection3.2.2.3asaresultofgaseouseffluentswillbecalculatedusingthedosefactorsofRegulatoryGuide1.109orthemethodology"."oftheODCM,asapplicalble.DosescalculatedfromenvironmentalsamplemediawillutilizethemethodologiesfoundinRegulatoryGuide1.109.4.3EvaluationofDosesFromDirectRadiationSection3.6.15.doftheTechnicalSpecificationsrequiresthatthedosecontributionasaresultofdirectradiationbeconsideredwhenevaluatingwhetherthedoselimitationsof40CFR190havebeenexceeded.
.lower.Forexample,I-131hasthesecondhighestcurie-to-dose factorequalto465mrem-sec/uCi-yr fortheinfantthyroid.Thiscorresponds toareleaseratelimitofapproximately 3nCi/sec.
1,*i"Prf+'<w+Xg'~Itplyg Directradiationdosesasaresultofthereactor,turbineandradwastebuildingsandoutsideradioactivestoragetanks(asapplicable)maybeevaluatedbyengineeringcalculationsorbyevaluatingenviromentalTLDresultsatcriticalreceptorlocations,siteboundaryorotherspecialinterestlocations.Forthe"evaluationofdirectradiation-doses-utilizingenvironmental'-TLDs,-':the'riticalreceptorinquestion,suchasthecriticalresidence,etc.,willbecomparedtothecontrollocations.ThecomparisoninvolvesthedifferenceinenvironmentalTLDresultsbetweenthereceptorlocationandtheaveragecontrollocationresult.4~4DosestoMembersofthePublicMithintheSiteBoundary.Section6.9.l.eoftheNineMilePointUnit1TechnicalSpecificationsrequiresthattheSemiannualRadioactiveEffluentReleaseReport~includeanassessmentoftheradiationdosesfromradioactiveliquidandgaseouseffluentstomembersofthepublicdue.to.their=,activitiesinsidethesiteboundaryasdefinedbyFigure5.1-1ofthespecifications.Amemberofthepublic,asdefinedbytheTechnicalSpecifications,wouldberepresentedbyanindividualwhovisits"thesites'nergyInformationCenterfor.thepurposeofobservingtheeducationaldisplaysorforpicnicing.andassociated...activities.  
3.2.2DoseCalculations willbeperformed monthlyataminimum,todemonstrate thatdosesresulting fromthereleaseofnoblegases,tritium,I-131,I-133andparticulates withhalflivesgreaterthan8daysarewithinthelimitsspecified in10CFR50,AppendixI.Theselimitsare:NobleGasAirDose5mrgamma/calendar quarter10mradbeta/calendar quarter10mrgamma/calendar year'0mradbeta/calendar yearRadioiodines, Tritium&Particulates 7.5mremtoanyorgan/calendar quarter"'15'mrem-to anyorgan/calendar.
>>r<<III~>>rn<<>>y>>f0''4~>>4s0V~<<.g<<g*WWy--,'>>>>>><<I~>><<,S>><<S'4P~"gag,>>
year 4NQSiI<<4.4I 3.2.2.1NobleGasAirDose-''-The-air'doseatthecritical.
4~4(Cont'd)FishingisamajorrecreationalactivityintheareaandontheSiteasaresultofthesalmonidandtroutpopulationsinLakeOntario.FishermenhavebeenobservedfishingattheshorelineneartheEnergyInformationCenterfromAprilthrough"Decemberinallweather'onditions."'Thus,"fishingis-the'ajoractivityperformedbymembersofthepublicwithinthesiteboundary.Basedonthenatureofthefishermenandundocumentedobservations,itisconservativelyassumed'hatthemaximumexposedindividualspendsanaverageof8hoursperweekfishingfromtheshorelineatalocationbetweentheEnergyInformationCenterandtheUnitlfacility.ThisestimateisconsideredconservativebutnotnecessarilyexcessiveandaccountsforoccasionswhereindividualsmayfishmoreonweekendsoronafewdaysinMarchoftheyear.Thepathwaysconsideredfortheevaluationincludetheinhalation""-''pathwaywiththeresultantlungdose,thegrounddosepathwaywiththeresultantwholebodyandskindoseandthedirectradiationdosepathwaywiththeassociatedtotalbodydose.Thedirectradiationdosepathway,in.actuality,includesseveralpathways.Theseinclude:thedirectradiationgammadosetoanindividualfromanoverheadplume,agammasubmersionplumedose,possibledirectradiationdosefromthefacilityandagroundplanedose(deposition).Becausethelocationisincloseproximitytothesite,anybetaplumesubmersiondoseisfelttobeinsignificant.  
receptorduetonoblegasreleasesisdetermined asfollows:Forgammaradfation Dg3.17x107MiX/QForbetaradiation D<~3.17x10E'iX/QQiwhereMairgammadosefactorin(mr/yearperuCi/m)for3i.eachisotopei(Table4-1)3N~airbetadosefactor(mrad/year peruCi/m)foreachisotopei(Table4-1)X/Qtherelativeplumeconcentration (inunitsofsec/m)atthelandsectorsiteboundaryor3beyond.Eitheraveragemeteorological data(Table3-1orAppendixC),orrealtimevaluesmaybeassumed."Elevated" X/Qvaluesareusedforstackreleases; "Ground"X/Qvaluesareusedfor;Emergency Condenser Ventreleases.
'iAW'II~4I'I~.(-I.lI"~p~II++II.>>l~Ili~gWyrIN'i~"Iwl~fI 4~4(Cont'd)Otherpathways,suchastheingestionpathway,arenotapplicable.Inaddition,pathwaysassociatedwithwaterrelatedrecreationalactivities,otherthanfishing,arenotapplicablehere.Theseincludeswimming,'oatingandwadingwhichareprohibitedatthe~facility.Theinhalationpathwayisevaluatedbyidentifyingtheapplicableradionuclides(radioiodine,tritiumandparticulates)intheeffluentfortheappropriatetimeperiod.,TheradionuclideconcentrationsarethenmultipliedbytheappropriateX/Qvalue,inhalationdosefactor,airintakerate,andthefractionalportionoftheyearinquestion.Thus,theinhalationpathwayisevaluatedusingthefollowingequationadaptedfromRegulatoryGuide1.109.NOTE:ThefollowingequationisadaptedfromequationsC-3andC-4ofRegulatoryGuide1.109.SincemanyofthefactorsareinunitsofpCi/m,,m/sec.,etc.,andsincethe33Fradionuclidedecayexpressionshavebeendeletedbecauseoftheshortdistancetothereceptorlocation,theequation...presentedhere,is.,not.identical.totheRegulatoryGuideequations.R~y.i[CFX/QDFA.Rt]ii]aawhere:Rthemaximumdosefortheperiodinquestiontothelung(j)forallradionuclides<i)fortheadultagegroup<a)inmrempertimeperiod.
Q~thetotalquantityofisotopeireleasedduring.theperiod,(pCi)-83.17x10-~theinverseofthenumberofsecondsinayear.
4~fPIIIk~s,A 4'(Cont'd)The'averageconcentrationinthestackreleaseofradionuclideiinpCi/mfortheperiodinquestion.3F~Unit1averagestackflowrateinm/sec.3'X/Q.The:plumedispersion"parameterforalocationapproximately0.50mileswestofNMP-1(Theplumedispersionparameteris8.9E-06andwasobtainedfromtheC.T.MainfiveyearaverageannualX/Qtables.AX/Qvaluebasedonrealtimemeteorologymayalsobeutilizedfortheperiodinquestion,ifdesired.Thestack(elevator)X/Qisconservativewhenbasedon0.50milesbecauseofthecloseJproximityofthestackandthereceptorlocation).DFAi)theinhalationdosefactorforradionuclidei,thelungj,andadultagegroupainmremperpCifoundonTableE-7ofRegulatoryGuide1.109.RaannualairintakeforindividualsinagegroupainMperyear(thisvalueis8,000mperyearand33wasobtained.fromTableE-5ofRegulatoryGuide1.109).fractionalportionoftheyearforwhichradionuclide-iwasdetectedandforwhichadoseistobecalculated(inyears).
4V'fe 3.2.2.2Radioiodine, Tritium&Particulates Thedosestoanindividual fromI-131,I-133,tritium,andparticulates withhalflivesgreaterthan8dayswillbecalculated asfollows:-8Dose3.17x10R~EiRi~akW~Qi WhereWJdispersion parameter eitherX/Q(sec/m)orD/Q3(1/m)depending onpathwayandreceptorlocation2assumed.Eitheraveragemeteorological data(Table3-1,orAppendixC)orrealtimevaluesmaybeassumed."Elevated" Wvaluesareusedforstackreleases; "Ground"WvaluesareusedforEmergency Condenser Ventreleases.
I$tVhH,~t'rP4)+'%Su' Thegrounddosepathway(deposition)willbeevaluatedbyobtainingatleastonesoilorshorelinesedimentsampleintheareawherefishingoccurs.Thedosewillthenbecalculatedusingthesampleresults,thetimeperiodinquestion,andthemethodologybasedonRegulatoryGuide1.109aspresentedinSection4.1.Theresultantdosemaybeadjustedforabackground-dosebysubtractingthe""-applicable-off-si'tecontrolsoilor=shorelinesedimentsampleradionuclideactivities.Intheeventitisnotedthatfishingisnotperformedfromtheshoreline,butisinsteadperformedinthewater(i.e.,theuseofwaders),thenthegrounddosepathway(deposition)willnotbeevaluated.Thedirectradiationgammadosepathwayincludesanygammadosesfromanoverheadplume,submersionintheplume,possibleradiationfromthefacilityandgroundplanedose(deposition).ThisgeneralpathwaywillbeevaluatedbyaverageenvironmentalTI,Dreadings.AtleasttwoenvironmentalTIDswillbeutilizedatonelocationinthe'approximateareawherefishingoccurs.TheTIDswillbeplacedinthefieldonapproximatelythebeginningofeachcalendarquarterandremovedonapproximatelytheendofeachcalendarquarter(quarter2,3,and4),.TheaverageTLDreadingswillbeadjustedbytheaveragecontrolTLDreadings.Thisisaccomplishedbysubtractingtheaveragequarterly;controlTI.DvaluefromtheaveragefishinglocationTLDvalue.TheapplicablequarterlycontrolTLDvalueswillbeutilizedafteradjustingfortheappropriatetimeperiod(asapplicable).ZntheeventoflossortheftoftheTLDs,resultsfromaTLDorTLDsintheareamaybeutilized.
thetotalquanityofisotopeireleasedduringtheperiod,(uCi)izaak3':17;x10thedosefactorforeachisotopei,pathwayj,agegroupa,andorgank(Table4-2,through4-20)~theinverseofthenumberofsecondsinayearTheRvaluescontained
l,RIk-)Lj'bgrjf 5.0ENVIRONMENTALMONITORINGPROGRAM5'SamplingStationsThecurrentsamplinglocationsarespecifiedinTable5-1andFiguresS.l-l,5.1-2.ThemeterologicaltowerisshowninFigure5.1-1.The.locationisshownas"TLD'ocation17.TheRadiologicalEnvironmentalMonitoringProgramisajointeffortbetweentheNiagaraMohawkPowerCorporationandtheNewYorkPowerAuthority,theownersand,operatorsoftheNineMilePointUnit1andtheJamesA.FitzPatrickNuclearPowerPlant,respectively.Samplinglocationsarechosenonthebasisofhistoricalaveragedispersionordepositionparametersfrombothunits.TheenvironmentalsamplinglocationcoordinatesshownonTable5-1arebasedontheNMP-2reactorcenterline.Theaveragedispersionanddepositionparametershavebeencalculatedfora5yearperiod,1978through1982.Thesedispersion'"""-'calculationsareattachedasAppendixC.Thecalculateddispersionordepositionparameterswillbecomparedtotheresultsoftheannuallandusecensus.Ifitisdeterminedthatamilksamplinglocationexistsatalocationthatyieldsasignificantlyhigher(e.g.50%)calculatedD/Qrate,thenewmilksamplinglocationwillbeaddedtothemonitoringprogramwithin30days~Ifanewlocationisadded,theoldlocationthatyieldsthelowestcalculatedD/QmaybedroppedfromtheprogramafterOctober31ofthatyear.  
.in'Tables,4-2,through 4-20werecalculated usingthemethodology definedinNUREG-0133,and Regulatory Guide1.109,Revision1.  
~Ef 5.2InterlaboratoryComparisonProgramAnalysesshallbeperformedonsamplescontainingknownquantitiesofradioactivematerialsthataresuppliedaspartofaCommissionapprovedorsponsoredInterlaboratoryComparisonProgram,such,asthe"EPACrosscheck'Program."-Participationshallbeonly'orthosemedia,e.g.,air,milk,water,etc.,-thatareincludedintheNineMilePointEnvironmentalMonitoringProgramandforwhichcrosschecksamplesareavailable.AnattemptwillbemadetoobtainaQCsampletoprogramsampleratioof5%orbetter.ThesiteidentificationsymbolortheactualQualityControlsampleresultsshallbereportedintheAnnualRadiologicalEnvironmentalOperatingReportsothattheCommissionstaffmayevaluatetheresults.SpecificsamplemediaforwhichEPACrossCheckProgramsamplesareavailableincludethefollowing:~grossbetainairparticulatefilters-~'ammaemittersinairparticulatefiltersI-131inmilkgammaemittersinmilk-gammaemittersinfoodproductgammaemittersinwatertritiuminwaterI-131inwater v'$g$A)Ifan%f'~1 5.3CapabilitiesforThermoluninescentDosimetersUsedforEnvironmentalMeasurementsRequireddetectioncapabilitiesforthermoluminescentdosimetersusedforenvironmentalmeasurementsrequiredbyTable4.6.20-1,footnoteb'*'-.oftheTechnicalSpecifications-,iare..based.;,on.ANSIStandard.N545,';~..-.>'",section4;3."-'"TLDsare'efinedasphosphorspackagedforFielduse.>,'nregardtothedetectioncapabilitiesforthermoluminescentdosimeters,onlyonedeterminationisrequiredtoevaluatetheabove.~capabilitiespertypeofTLD.Furthermore,theabovecapabilitiesmaybedeterminedbythevendorwhosuppliestheTLDs.Requireddetectioncapabilitiesareasfollows:5.3.1UniformityshallbedeterminedbygivingTLDsfromthesamebatchanexposureequaltothatresultingfromanexposurerateof10uR/hrduringthefieldcycle.Theresponsesobtainedshallhavearelativestandarddeviationoflessthan7.5%.Atotalofatleast5TLDs4i,'~"shallbe.evaluated.5.3.2ReproducibilityshallbedeterminedbygivingTLDsrepeatedexposures'"equalto,thatresultingfromanexposurerateof10uR/hrduringthe'ieldcycle.The..average,oftherelative'standard"deviationsof,theresponsesshallbelessthan3.0%.htotalofatleast4TLDsshall,beevaluated.
-~4W 3.2.2.3Accumulating DosesDoseswillbecalculated monthly,ataminimum,forgammaairandbetaair,theidentified criticalorgan,andagegroup.Resultswillbesummedforeachcalendarquarterandyear.Ithasbeenhistorically demonstrated thatthecriticalpathwayisusuallythegrass-cow-milk pathwayandthecriticalorganis,the.,,infant',s thyroid.Forthisreason,monthlyinfantthyroiddoseestimates willnormallybemadepriortoreceiptofallanalysisdata(i.e.,strontium andtritium).
f}IIIl4e 5.3.3DependenceofexposureinterpretationonthelengthofafieldcycleshallbeexaminedbyplacingTLDsforaperiodequaltoatleastafieldcycleandaperiodequaltohalfthesamefieldcycleinanareawheretheexposurerateisknowntobeconstant.Thistestshallbeconductedunderapproximateaveragewintertemperatures,and,:approximateaverage..summertemperatures.Forthesetests,.theratio'oftheresponse"-obtainedinthefieldcycletotwicethatobtainedforhalfthefieldcycleshallnotbelessthan0.85.Atleast6TLDsshallbeevaluated5.3.4'nergydependenceshallbeevaluatedbytheresponse.ofTLDstophotonsforseveralenergiesbetweenapproximately30keVand3MeV.Theresponseshallnotdifferfromthatobtainedwiththecalibration'sourcebymorethan25%forphotonswithenergiesgreaterthan80keVandshallnotbeenhancedbymorethanafactoroftwoforphotonswithenergieslessthan80keV.Atotalofatleast8TLDsshallbeevaluated.5.3.5ThedirectionaldependenceoftheTLDresponseshallbedeterminedbycomparingtheresponseoftheTLDexposedintheroutineorientation'*'"withrespecttothecalibrationsourcewiththeresponseobtainedfor"'di'fferent-orientations;*To"accomplishthis,-the,TLD-shall.be.,rotatedthroughatleasttwoperpendicularplanes.'heresponseaveraged-overalldirectionsshallnotdifferfromtheresponseobtainedinthestandardcalibrationpositionbymorethan1(C.Atotalofatleast4TLDsshallbeevaluated.  
Thecriticaldosesarebasedonthe,following pathways:
~<4~g.'t 5.3.6LightdependenceshallbedeterminedbyplacingTLDsinthefieldforaperiodequaltothefieldcycleunderthefourconditionsfoundinANSIN545,section4.3.6.TheresultsobtainedfortheunwrappedTLDsshallnotdifferfromthoseobtainedfortheTLDswrappedinaluminumfoilbymorethan10K.Atotalofatleast4TLDsshallbeevaluatedforeachofthefourconditions.5.3;7'''Moisture'dependence'shall"be-determined"by-placing=TLDs.(thatis,the''.phosphors~packaged"forfielduse)foraperiodequaltothefield,...-cycleinanareawheretheexposurerateisknowntobeconstant.TheTLDsshallbeexposedundertwoconditions:(1)packagedinathin,sealedplasticbag,and(2)packagedinathin,sealedplasticbagwithsufficientwatertoyieldobservable'oisturethroughoutthe.fieldcycle.TheTLDorphosphor,asappropriate,shallbedriedbeforereadout.TheresponseoftheTLDexposedintheplasticbagcontainingwatershallnotdifferfromthatexposedintheregularplasticbagbymorethan10X.Atotalofatleast4TLDsshallbeevaluatedforeachcondition.'."5;3".8.-"a'Self.irradiationshallbedeterminedbyplacingTLDsforaperiodequaltothefieldcycleinanareawheretheexposurerateislessthan10uR/hrandtheexposureduringthefieldcycleisknown.Ifnecessary,.correctionsshallbeappliedforthedependenceof'exposureinterpretationon*thelengthofthefieldcycle(ANSIN545,.section4.3.3).The'averageexposureinferredfromtheresponsesof-theTLDsshallnotdifferfromtheknownexposurebymorethananexposureequaltothatresultingfromanexposurerateof10uR/hrduringthefieldcycle.Atotalofatleast3TLDsshallbeevaluated.
noblegasplumeairdosegroundplanedose(deposition) inhalation dosecow'smilkdosegoat'smilkdosemeatconsumption dosevegetation (foodcrops)doseThequarterly andannualresultsshallbecomparedtothelimitslistedin'.paragraph 3.2.2.Ifthelimitsareexceeded, specialreports,asrequiredbySection.6.9.3 of-theTechnical Specification, shallbesubmitted.
If''I<<gr TABLEl-lRVALUESFORTHENINEMILEPOINTUNIT1FACILITYapjiNUCLIDE89Sr90Sr134Cs137Cs58Co60Co54HCr-51Fe-59Zn-65Zr-95I-131I-133Cs-136Ba-140Ce-141'e-55Ni-63ADULT-TOTALBODYR~i{MREM/YR-Cx2.05E-34.37E-11.89E+01.12E+06.47E-41.85E-32.72E-37.40E-74.05E-63.01E-31.09E-l1.69E-73'4E-43.53E-52'3E-13..92E-55.49E-93.47E-43.41E-3TEEN-LIVER-,I-"N/AN/A2.35E+01.78E+02.87E-48.38E-41.40E-25.69E-7N/A8.03E-32.37E-12.53E-76.65E-41.22E-43.80E-17.81'-75.17E-8.1.60E-37.46E-3<<58-  
kl~A~4~gt4p~'J-4I''fi 3.3CriticalReceptors Inaccordance withtheprovisions of10CFR20and10CFR50,AppendixI,thecriticalreceptors havebeenidentified andarecontained inTable3-1..."For...noble gas:doses, one.oftwocriticalreceptorlocations willbeassumed.WhenmaximumfiveyearaverageannualX/Qvaluesareused,thecriticalreceptoristhemaximumX/Qlandsectorsiteboundary1interface.
Whenrealtimemeteorological X/Qvaluesareused,thecriticalreceptormayeitherbethemaximumX/Qlandsectorsiteboundarylocation, orthedownwindlocationofgreatestX/Qresidence (e.g.,1.5mileseast),whichever ishigher.ForI-133,I-131,tritiumandparticulate radionuclides withhalflifegreaterthaneightdays,thecriticalpathwaysaremilk(cowandgoat>,meat,vegetation, inhalation anddirectradiation (groundplane)asaresultofgrounddeposition.
ThecowmilkandgoatmilkpathwaywillbebasedonthegreatestD/Q~...*'ilk,.cow andmilkgoatlocationasdetermined bytechnical specification'.3.6.22.',.The'inhalation
'dosepathway,will.bebased-onthegreatestX/Qresidence asdetermined bytechnical specification 3.6.22sincethislocationwouldhavethegreatestpotential occupancy time.Thegroundplanedosepathwaywillbecalculated asthegreatestD/Qresidence becauseofthegreatestpotential occupancy time.-38" lp4l\Ci$il+i' 3.3(Cont'd)Forthemeatconsumption dosepathway,thecriticalreceptoristhegreatestD/Qmeatanimallocation.
Thislocationhasbeendetermined inconjunction withthelandusecensus(technical specification 3.6.22)andissubjecttochange.Thevegetation (foodcrop)doseisbasedonthegreatest-D/Q gardenlocationfromwhichsamplesare.taken.Thislocationalso.maybemodified:as aresult.of.vegetation samplingsurveys.3.4Refinement ofOffsiteDosesResulting fromEmergency Condenser VentReleasesThedosesresulting fromtheoperation oftheemergency condensers andcalculated inaccordance with3.2.2mayberefinedusingdatafromactualenviromental samples.Grounddeposition sampleswillbeobtainedfromanareaorareasofmaximumprojected deposition.
Theseareasareanticipated tobeat<,<or..near.
thesiteboundaryandnearprojected plumecenterline.
Usingthemethodology foundinRegulatory Guide1.109,thedosewillbecalculated tothemaximumexposedindividual.
Thisdosewillthenbecomparedtothedosecalculated inaccordance with3.2.2.Thecomparison willresult,inanadjustment factoroflessthanor.greaterthanonewhichwillbeusedtoadjust"the'other dosesfromotherpathways.  
+jl..LS 3.4(Cont'd)Otherenvironmental samplesmayalsobecollected andtheresultant calculated dosestothemaximumexposedindividual comparedtothedosecalculated per3.2.2.Otherenvironmental samplemediamayincludemilk,vegetation (suchasgardenbroadleaf vegetables),
etc.'"."Theadjustment:factors.
from.these.pathways maybeappliedtothedosescalculated per3;2.2onapathwaybypathwaybasisorseveralpathwayadjustment factorsmaybeaveragedandusedtoadjustcalculated doses.Dosescalculated fromactualenvironmental samplemediawillbebasedonthemethodology presented inRegulatory Guide1.109.Theregulatory guideequations maybeslightlymodifiedtoaccountforshortintervals oftime(lessthanoneyear)ormodifiedforsimplicity purposesbydeletingdecayfactors.Deletionofdecayfactorswouldyieldmoreconservative results.  
~~~'a  
 
==4.0 40CFR190REQUIREMENTS==
The"UraniumFuelCycle"isdefinedin40CFRPart190.02(b)asfollows:-"Uraniumfuelcycle'eans theoperations ofmillingofuraniumore,chemical-conversion ofuranium,isotopic-enrichment ofuranium,fabrication ofuraniumfuel,generation ofelectricity byalight-water-cooled nuclearpowerplantusinguraniumfuel,andreprocessing ofspenturaniumfuel,totheextentthatthesedirectlysupporttheproduction ofelectrical'ower forpublicuseutilizing nuclearenergy,butexcludesminingoperations, operations
.atwastedisposalsites,transportation ofanyradioactive materialinsupport.oftheseoperations, andthereuseofrecovered non-uranium specialrnuclearandby-product materials fromthecycle."Section3.6.15.doftheTechnical Specifications requiresthatwhen~'.thecalculated dosesassociated withtheeffluentreleasesexceedtwicethelimitsofsections3.6.15.a.(2)(b),
3.6.15.b.(2)(b) and3.6.15.b.(3)(b),
thencalculations shallbemadeincluding directradiation contributions fromthereactorunitsand.outside storagetanks(asapplicable)-
todetermine whetherthe40CFR190dose-limitshavebeenexceeded.  
~~~"0Eff,ffE'~~IfkEI~'kI'II~PIEQ',WEE,Wt~IFEIFJIfJj4I'00fIJI~~FfFQf 4.0(Cont'd)Ifsuchisthecase,NiagaraMohawkshallsubmitaSpecialReporttotheNRCandlimitsubsequent releasessuchthat.thedosecommitment toarealindividual fromalluraniumfuelcyclesourcesislimitedto<'25mremtothe'total bodyor-anyorgan--(except-the,.thyroid,
'which'islimitedto<..75mrem)overthecalendaryear.Thisreportistodemonstrate thatradiation exposures toallrealindividuals fromalluraniumfuelcyclesources(including allliquidandgaseouseffluentpathwaysanddirectradiation) arelessthanthelimitsin40CFRPart190.Ifreleasesthatresultindosesexceeding the40CFR190limitshaveoccurred, thenavariancefromtheNRCtopermitsuchreleaseswillberequested andifpossible, actionwillbetakentoreducesubsequent releases.
""'"The"reporttotheNRCshallcontain:1)Identification ofalluraniumfuelcyclefacilities or'perations within5milesofthenuclearpowerreactorunitsatthesitethatcontribute to,the-annual doseofthemaximumexposedmemberofthepublic.2)Identification ofthemaximumexposedmemberofthepublicandadetermination ofthetotalannualdosetothispersonfromexistingpathwaysandsourcesofradioactive effluents anddirectradiation.
<<42-J'-~4~>f4p 4.0(Cont'd)Themaximumtotalbodyandorgandosesresulting fromradioactive
-material inliquideffluents fromNineMilePointUnit1will.besummedwiththemaximumdosesresulting fromthereleasesofnoblegases,radioiodines, andparticulates fortheothercalendarquarters~>>~--(as.applicable)...and, from.thecalendar.,quarter in,whichtwicethe..limitwasexceeded.
Thedirectdosecomponents willbedetermined byeithercalculation oractualmeasurement.
Actualmeasurements willutilizeenvironmental TLDdosimetry.
Calculated measurements willutilizeengineering calculations todetermine aprojected directdosecomponent.
Zntheeventcalculations areused,themethodology willbedetailedasrequiredinSection6.9.1.eoftheTechnical Specifications.
ThedosesfromNineMilePointUnit1willbeaddedtothedosestothemaximumexposedindividual thatarecontributed fromotheruraniumfuelcycleoperations within5milesofthesite.Forthepurposeofcalculating doses,'he resultsoftheRadiological Enviromental Monitoring Programmaybeincludedforproviding morerefinedestimates ofdosesto.areal.maximumexposedindividual;..
Estimated doses,ascalculated fromstationeffluents, maybereplacedbydosescalculated fromactualenviromental sampleresults.  
~e~~eeee~~~eeeIeeeDEeeeeeeeee Evaluation ofDosesFromLiquidEffluents Fortheevaluation ofdosestorealmembersofthepublicfromliquideffluents, thefishconsumption andshoreline sedimentgrounddosewillbeconsidered.
Sincethedosesfromotheraquaticpathwaysareinsignificant, fi'sh'onsumption'and "shoreline'ediment>>
aretheonly'wopathwaysthatwill-beconsidered.
Thedoseassociated with,fishconsumption maybecalculated usingeffluentdataandRegulatory Guide1.109methodology orbycalculating adosetomanbasedonactualfishsampleanalysisdata.Thedoseassociated withshoreline sedimentisbasedontheassumption thattheshoreline wouldbeutilizedasarecreational area.ThisdosemaybederivedfromliquideffluentdataandRegulatory Guide1.109methodology orfromactualshoreline sedimentsampleanalysisdata.Equations usedtoevaluatedosesfromactualfishandshoreline sedimentsamplesarebasedonRegulatory Guide1.109methodology.
.Because.
ofthesamplemediumtypeandthehalf-lives oftheradionuclides historically
: observed, thedecaycorrected portionsoftheequations aredeleted.Thisdoesnotreducetheconservatism ofthecalculated dosesbutincreases thesimplicity fromanevaluation pointofview.Thedosefromfishsamplemediaiscalculated as:(1)Rwb~Fi[Cifxux1000xDiwbxf]Where:~Thetotaldosetothewholebodyofanadultinmremperyear.
A<<+t%eA (Cont'd)Cif~Theconcentration ofradionuclide iinfishsamplesinpCi/gram.
~Theconsumption rateoffishforanadult(21kgperyear).1000~Gramsperkilogram'Diwb~Thedosefactorforradionuclide::i forthewholebodyofanadult(R.G.1.109,TableE-11).~Thefractional portionoftheyearoverwhichthedoseisapplicable.
(2)RlWhere:~~i[Cifxyx1000xDilx~Thetotaldosetotheliverofanadult(maximumexposedorgan)inmremperyear.Cif=Theconcentration ofradionuclide iinfishsamplesinpCi/gram.
~Theconsumption rateoffishforanadult(21kgperyear).1000~GramsperkilogramDil~Thedosefactorforradionuclide ifortheliverofanadult(R.G.1.109,TableE-ll)~Thefractional portionoftheyearoverwhichthedoseisapplicable.
Thedosefromshoreline sedimentsamplemediaiscalculated as:Where:-E[Ci,xllx-40,000x0.3xDiwbxf]and~g[Cisxyx40,000x0.3xDiskxf]~Thetotaldosetothewholebodyofateenageroradult(maximumexposedagegroup),inmremperyear.Rsk~Thetotaldosetotheskinofateenageroradult(maximumexposedagegroup)inmremperyear.Cis~The-concentration ofradionuclide iinshoreline sedimentinpci/gram.
4"0AgR)i"I (Cont'd)~Theusagefactor.Thisisassumedas67hoursperyearbyateenageroradult.I40,000~Theproductoftheassumeddensityofshoreline sediment(40kilogrampersquaremetertoadepthof2.5cm)timesthenumberofgramsperkilogram.
0.3~Theshorewidthfactorforalake,Diwb=The'dosefactorfor'radionuclide iforthetotal,body(R.G.1.109,TableE-6)Disk~Thedosefactorforradionuclide ifortheskin(R.G.1.109,TableE-6)~Thefractional portionoftheyearoverwhichthedoseisapplicable.
NOTE:"'ecauseofthenatureofthereceptorlocationandtheextensive fishingactivityinthearea,thecriticalindividual-may beateenageroranadult.
Qb.~iiIh'4*~~~'ial4lhkgtlXfCkingil0~iii\f1E1'h'4gt0tl~iit4 4.2Evaluation ofDosesFromGaseousEffluents Fortheevaluation ofdosestorealmembersofthepublicfromgaseouseffluents, thepathwayscontained insection3.2.2.3oftheODCMwillbeconsidered.
Theseincludetheingestion, inhalation and'deposition pathways'.
However,anyupdatedfield:data may.beutilizedthatconcernslocations ofrealindividuals, realtimemeteorological data,locationofcriticalreceptors, etc.Datafromthemostrecentcensusandsamplelocationsurveysshouldbeutilized.
Dosesmayalsobecalculated fromactualenviromental samplemedia,asavailable.
Enviromental samplemediadatasuchasTID,airsample,milksampleandvegetable (foodcrop)sampledatamaybeutilizedinlieuofeffluentcalculational data.Dosestomemberofthepublicfromthepathwasycontained inODCMsection3.2.2.3asaresultofgaseouseffluents willbecalculated usingthedosefactorsofRegulatory Guide1.109orthemethodology
"."oftheODCM,asapplicalble.
Dosescalculated fromenvironmental samplemediawillutilizethemethodologies foundinRegulatory Guide1.109.4.3Evaluation ofDosesFromDirectRadiation Section3.6.15.doftheTechnical Specifications requiresthatthedosecontribution asaresultofdirectradiation beconsidered whenevaluating whetherthedoselimitations of40CFR190havebeenexceeded.
1,*i"Prf+'<w+X g'~Itplyg Directradiation dosesasaresultofthereactor,turbineandradwastebuildings andoutsideradioactive storagetanks(asapplicable) maybeevaluated byengineering calculations orbyevaluating enviromental TLDresultsatcriticalreceptorlocations, siteboundaryorotherspecialinterestlocations.
Forthe"evaluation ofdirectradiation-doses-utilizing environmental'-TLDs,
-':the'ritical receptorinquestion, suchasthecriticalresidence, etc.,willbecomparedtothecontrollocations.
Thecomparison involvesthedifference inenvironmental TLDresultsbetweenthereceptorlocationandtheaveragecontrollocationresult.4~4DosestoMembersofthePublicMithintheSiteBoundary.
Section6.9.l.eoftheNineMilePointUnit1Technical Specifications requiresthattheSemiannual Radioactive EffluentReleaseReport~include anassessment oftheradiation dosesfromradioactive liquidandgaseouseffluents tomembersofthepublicdue.to.their=,activities insidethesiteboundaryasdefinedbyFigure5.1-1ofthespecifications.
Amemberofthepublic,asdefinedbytheTechnical Specifications, wouldberepresented byanindividual whovisits"thesites'nergy Information Centerfor.thepurposeofobserving theeducational displaysorforpicnicing
.andassociated
...activities.  
>>r<<III~>>rn<<>>y>>f0''4~>>4s0V~<<.g<<g*WWy--,'>>>>>><<
I~>><<,S>><<S'4P~"gag,>>
4~4(Cont'd)Fishingisamajorrecreational activityintheareaandontheSiteasaresultofthesalmonidandtroutpopulations inLakeOntario.Fishermen havebeenobservedfishingattheshoreline neartheEnergyInformation CenterfromAprilthrough"December inallweather'onditions."
'Thus,"fishingis-the'ajor activityperformed bymembersofthepublicwithinthesiteboundary.
Basedonthenatureofthefishermen andundocumented observations, itisconservatively assumed'hatthemaximumexposedindividual spendsanaverageof8hoursperweekfishingfromtheshoreline atalocationbetweentheEnergyInformation CenterandtheUnitlfacility.
Thisestimateisconsidered conservative butnotnecessarily excessive andaccountsforoccasions whereindividuals mayfishmoreonweekendsoronafewdaysinMarchoftheyear.Thepathwaysconsidered fortheevaluation includetheinhalation
""-''pathway withtheresultantlung dose,thegrounddosepathwaywiththeresultant wholebodyandskindoseandthedirectradiation dosepathwaywiththeassociated totalbodydose.Thedirectradiation dosepathway,in.actuality, includesseveralpathways.
Theseinclude:thedirectradiation gammadosetoanindividual fromanoverheadplume,agammasubmersion plumedose,possibledirectradiation dosefromthefacilityandagroundplanedose(deposition).
Becausethelocationisincloseproximity tothesite,anybetaplumesubmersion doseisfelttobeinsignificant.  
'iAW'II~4I'I~.(-I.lI"~p~II++II.>>l~Ili~gWyrIN'i~"Iwl~fI 4~4(Cont'd)Otherpathways, suchastheingestion pathway,arenotapplicable.
Inaddition, pathwaysassociated withwaterrelatedrecreational activities, otherthanfishing,arenotapplicable here.Theseincludeswimming,'oating andwadingwhichareprohibited atthe~facility.
Theinhalation pathwayisevaluated byidentifying theapplicable radionuclides (radioiodine, tritiumandparticulates) intheeffluentfortheappropriate timeperiod.,Theradionuclide concentrations arethenmultiplied bytheappropriate X/Qvalue,inhalation dosefactor,airintakerate,andthefractional portionoftheyearinquestion.
Thus,theinhalation pathwayisevaluated usingthefollowing equationadaptedfromRegulatory Guide1.109.NOTE:Thefollowing equationisadaptedfromequations C-3andC-4ofRegulatory Guide1.109.SincemanyofthefactorsareinunitsofpCi/m,,m/sec.,etc.,andsincethe33Fradionuclide decayexpressions havebeendeletedbecauseoftheshortdistancetothereceptorlocation, theequation...presented here,is.,not.identical
.totheRegulatory Guideequations.
R~y.i[CFX/QDFA.Rt]ii]aawhere:Rthemaximumdosefortheperiodinquestiontothelung(j)forallradionuclides
<i)fortheadultagegroup<a)inmrempertimeperiod.
4~fPIIIk~s,A 4'(Cont'd)The'average concentration inthestackreleaseofradionuclide iinpCi/mfortheperiodinquestion.
3F~Unit1averagestackflowrateinm/sec.3'X/Q.The:plume dispersion"parameter foralocationapproximately 0.50mileswestofNMP-1(Theplumedispersion parameter is8.9E-06andwasobtainedfromtheC.T.MainfiveyearaverageannualX/Qtables.AX/Qvaluebasedonrealtimemeteorology mayalsobeutilizedfortheperiodinquestion, ifdesired.Thestack(elevator)
X/Qisconservative whenbasedon0.50milesbecauseofthecloseJproximity ofthestackandthereceptorlocation).
DFAi)theinhalation dosefactorforradionuclide i,thelungj,andadultagegroupainmremperpCifoundonTableE-7ofRegulatory Guide1.109.Raannualairintakeforindividuals inagegroupainMperyear(thisvalueis8,000mperyearand33wasobtained.fromTableE-5ofRegulatory Guide1.109).fractional portionoftheyearforwhichradionuclide-iwasdetectedandforwhichadoseistobecalculated (inyears).
I$tVhH,~t'rP4)+'%Su' Thegrounddosepathway(deposition) willbeevaluated byobtaining atleastonesoilorshoreline sedimentsampleintheareawherefishingoccurs.Thedosewillthenbecalculated usingthesampleresults,thetimeperiodinquestion, andthemethodology basedonRegulatory Guide1.109aspresented inSection4.1.Theresultant dosemaybeadjustedforabackground-dose bysubtracting the""-applicable
-off-si'te controlsoilor=shoreline sedimentsampleradionuclide activities.
Intheeventitisnotedthatfishingisnotperformed fromtheshoreline, butisinsteadperformed inthewater(i.e.,theuseofwaders),thenthegrounddosepathway(deposition) willnotbeevaluated.
Thedirectradiation gammadosepathwayincludesanygammadosesfromanoverheadplume,submersion intheplume,possibleradiation fromthefacilityandgroundplanedose(deposition).
Thisgeneralpathwaywillbeevaluated byaverageenvironmental TI,Dreadings.
Atleasttwoenvironmental TIDswillbeutilizedatonelocationinthe'approximate areawherefishingoccurs.TheTIDswillbeplacedinthefieldonapproximately thebeginning ofeachcalendarquarterandremovedonapproximately theendofeachcalendarquarter(quarter2,3,and4),.TheaverageTLDreadingswillbeadjustedbytheaveragecontrolTLDreadings.
Thisisaccomplished bysubtracting theaveragequarterly; controlTI.DvaluefromtheaveragefishinglocationTLDvalue.Theapplicable quarterly controlTLDvalueswillbeutilizedafteradjusting fortheappropriate timeperiod(asapplicable).
ZntheeventoflossortheftoftheTLDs,resultsfromaTLDorTLDsintheareamaybeutilized.
l,RIk-)Lj'bgrjf  
 
==5.0 ENVIRONMENTAL==
MONITORING PROGRAM5'SamplingStationsThecurrentsamplinglocations arespecified inTable5-1andFiguresS.l-l,5.1-2.Themeterological towerisshowninFigure5.1-1.The.locationisshownas"TLD'ocation 17.TheRadiological Environmental Monitoring ProgramisajointeffortbetweentheNiagaraMohawkPowerCorporation andtheNewYorkPowerAuthority, theownersand,operators oftheNineMilePointUnit1andtheJamesA.FitzPatrick NuclearPowerPlant,respectively.
Samplinglocations arechosenonthebasisofhistorical averagedispersion ordeposition parameters frombothunits.Theenvironmental samplinglocationcoordinates shownonTable5-1arebasedontheNMP-2reactorcenterline.
Theaveragedispersion anddeposition parameters havebeencalculated fora5yearperiod,1978through1982.Thesedispersion
'"""-'calculations areattachedasAppendixC.Thecalculated dispersion ordeposition parameters willbecomparedtotheresultsoftheannuallandusecensus.Ifitisdetermined thatamilksamplinglocationexistsatalocationthatyieldsasignificantly higher(e.g.50%)calculated D/Qrate,thenewmilksamplinglocationwillbeaddedtothemonitoring programwithin30days~Ifanewlocationisadded,theoldlocationthatyieldsthelowestcalculated D/QmaybedroppedfromtheprogramafterOctober31ofthatyear.  
~Ef 5.2Interlaboratory Comparison ProgramAnalysesshallbeperformed onsamplescontaining knownquantities ofradioactive materials thataresuppliedaspartofaCommission approvedorsponsored Interlaboratory Comparison Program,such,asthe"EPACrosscheck'Program."-Participation shallbeonly'orthosemedia,e.g.,air,milk,water,etc.,-thatareincludedintheNineMilePointEnvironmental Monitoring Programandforwhichcrosscheck samplesareavailable.
AnattemptwillbemadetoobtainaQCsampletoprogramsampleratioof5%orbetter.Thesiteidentification symbolortheactualQualityControlsampleresultsshallbereportedintheAnnualRadiological Environmental Operating ReportsothattheCommission staffmayevaluatetheresults.SpecificsamplemediaforwhichEPACrossCheckProgramsamplesareavailable includethefollowing:
~grossbetainairparticulate filters-~'ammaemittersinairparticulate filtersI-131inmilkgammaemittersinmilk-gammaemittersinfoodproductgammaemittersinwatertritiuminwaterI-131inwater v'$g$A)Ifan%f'~1 5.3Capabilities forThermoluninescent Dosimeters UsedforEnvironmental Measurements Requireddetection capabilities forthermoluminescent dosimeters usedforenvironmental measurements requiredbyTable4.6.20-1, footnoteb'*'-.oftheTechnical Specifications-,iare..based.;,on.
ANSIStandard.N545,';~..-.>
'",section4;3."-'"TLDsare'efined asphosphors packagedforFielduse.>,'nregardtothedetection capabilities forthermoluminescent dosimeters, onlyonedetermination isrequiredtoevaluatetheabove.~capabilities pertypeofTLD.Furthermore, theabovecapabilities maybedetermined bythevendorwhosuppliestheTLDs.Requireddetection capabilities areasfollows:5.3.1Uniformity shallbedetermined bygivingTLDsfromthesamebatchanexposureequaltothatresulting fromanexposurerateof10uR/hrduringthefieldcycle.Theresponses obtainedshallhavearelativestandarddeviation oflessthan7.5%.Atotalofatleast5TLDs4i,'~"shallbe.evaluated.
5.3.2Reproducibility shallbedetermined bygivingTLDsrepeatedexposures
'"equalto,thatresulting fromanexposurerateof10uR/hrduringthe'ieldcycle.The..average, oftherelative'standard" deviations of,theresponses shallbelessthan3.0%.htotalofatleast4TLDsshall,beevaluated.
f}IIIl4e 5.3.3Dependence ofexposureinterpretation onthelengthofafieldcycleshallbeexaminedbyplacingTLDsforaperiodequaltoatleastafieldcycleandaperiodequaltohalfthesamefieldcycleinanareawheretheexposurerateisknowntobeconstant.
Thistestshallbeconducted underapproximate averagewintertemperatures, and,:approximate average..summertemperatures.
Forthesetests,.theratio'oftheresponse"-obtained inthefieldcycletotwicethatobtainedforhalfthefieldcycleshallnotbelessthan0.85.Atleast6TLDsshallbeevaluated 5.3.4'nergydependence shallbeevaluated bytheresponse.ofTLDstophotonsforseveralenergiesbetweenapproximately 30keVand3MeV.Theresponseshallnotdifferfromthatobtainedwiththecalibration
'sourcebymorethan25%forphotonswithenergiesgreaterthan80keVandshallnotbeenhancedbymorethanafactoroftwoforphotonswithenergieslessthan80keV.Atotalofatleast8TLDsshallbeevaluated.
5.3.5Thedirectional dependence oftheTLDresponseshallbedetermined bycomparing theresponseoftheTLDexposedintheroutineorientation
'*'"withrespecttothecalibration sourcewiththeresponseobtainedfor"'di'fferent
-orientations;
*To"accomplish this,-the, TLD-shall.be.,rotated throughatleasttwoperpendicular planes.'heresponseaveraged-overalldirections shallnotdifferfromtheresponseobtainedinthestandardcalibration positionbymorethan1(C.Atotalofatleast4TLDsshallbeevaluated.  
~<4~g.'t 5.3.6Lightdependence shallbedetermined byplacingTLDsinthefieldforaperiodequaltothefieldcycleunderthefourconditions foundinANSIN545,section4.3.6.Theresultsobtainedfortheunwrapped TLDsshallnotdifferfromthoseobtainedfortheTLDswrappedinaluminumfoilbymorethan10K.Atotalofatleast4TLDsshallbeevaluated foreachofthefourconditions.
5.3;7'''Moisture'dependence'shall"be-determined"by-placing=TLDs.(that is,the''.phosphors~packaged "forfielduse)foraperiodequaltothefield,...-
cycleinanareawheretheexposurerateisknowntobeconstant.
TheTLDsshallbeexposedundertwoconditions:
(1)packagedinathin,sealedplasticbag,and(2)packagedinathin,sealedplasticbagwithsufficient watertoyieldobservable'oisture throughout the.fieldcycle.TheTLDorphosphor, asappropriate, shallbedriedbeforereadout.TheresponseoftheTLDexposedintheplasticbagcontaining watershallnotdifferfromthatexposedintheregularplasticbagbymorethan10X.Atotalofatleast4TLDsshallbeevaluated foreachcondition.
'."5;3".8.-
"a'Self.irradiation shallbedetermined byplacingTLDsforaperiodequaltothefieldcycleinanareawheretheexposurerateislessthan10uR/hrandtheexposureduringthefieldcycleisknown.Ifnecessary,.corrections shallbeappliedforthedependence of'exposureinterpretation on*thelengthofthefieldcycle(ANSIN545,.section4.3.3).The'average exposureinferredfromtheresponses of-theTLDsshallnotdifferfromtheknownexposurebymorethananexposureequaltothatresulting fromanexposurerateof10uR/hrduringthefieldcycle.Atotalofatleast3TLDsshallbeevaluated.
If''I<<gr TABLEl-lRVALUESFORTHENINEMILEPOINTUNIT1FACILITYapjiNUCLIDE89Sr90Sr134Cs137Cs58Co60Co54HCr-51Fe-59Zn-65Zr-95I-131I-133Cs-136Ba-140Ce-141'e-55Ni-63ADULT-TOTALBODYR~i{MREM/YR-Cx 2.05E-34.37E-11.89E+01.12E+06.47E-41.85E-32.72E-37.40E-74.05E-63.01E-31.09E-l1.69E-73'4E-43.53E-52'3E-13..92E-55.49E-93.47E-43.41E-3TEEN-LIVER-,I-"N/AN/A2.35E+01.78E+02.87E-48.38E-41.40E-25.69E-7N/A8.03E-32.37E-12.53E-76.65E-41.22E-43.80E-17.81'-75.17E-8.1.60E-37.46E-3<<58-  
,1tl4f(
,1tl4f(
TABLE1-2PARAMETERSFORTHELIQUIDEFFLUENTPATHWAYPARAMETERUapMpBipDaipiVALUEAdult~21.0Kg/yrTeen16.0Kg/yr0.2590,ft./second.EachElementEachradionuclideREFERENCE(REG.GUIDE1.109)TableE-5SiteSpecificSiteSpecificTableA-1TablesE-lltoE-14Tp26.9hoursSiteSpecific II',leAcP~Ak.
TABLE1-2PARAMETERS FORTHELIQUIDEFFLUENTPATHWAYPARAMETER UapMpBipDaipiVALUEAdult~21.0Kg/yrTeen16.0Kg/yr0.2590,ft./second.EachElementEachradionuclide REFERENCE (REG.GUIDE1.109)TableE-5SiteSpecificSiteSpecificTableA-1TablesE-lltoE-14Tp26.9hoursSiteSpecific II',leAcP~Ak.
TABLE2-1AverageEnergyPerDisintegrationISOTOPEAr-41Kr-83mKr-85Kr-85mKr-87Emev/dis1.2940.002480.00220.1590.793~Ref(3)EBmev/dis(40.4640.03710.2500.2531.325Ref)(3)Kr-881.950.377Kr-89Kr-90Xe-131MXe-133Xe-133mXe-135Xe-135m2.22'2.100.02010.04540.0420.2470.432(2)(2)1.371.010.1430.1350.3.90.3170.095(2)(2)Xe-137Xe-1380.194l.18'.640.611(1)ORNL-4923,RadioactiveAtoms-SulementI,M.S.Martin,November1973.(2)NEDO-12037,"SummaryofGammaandBetaEmittersandIntensityData";M.E.""',".Meek,R.S.'Gilbert,January1970.(The.averageenergy..wascomputedfrom-'themaximumenergyusing.theICRPIIequation,.notthe.1/3value..assumptionusedinthisreference).(3)NCRPReportNo.58,"AHandbookofRadioactivityMeasurementsProcedures";1978(4)Theaverageenergyincludesconversionelectrons.
TABLE2-1AverageEnergyPerDisintegration ISOTOPEAr-41Kr-83mKr-85Kr-85mKr-87Emev/dis1.2940.002480.00220.1590.793~Ref(3)EBmev/dis(4 0.4640.03710.2500.2531.325Ref)(3)Kr-881.950.377Kr-89Kr-90Xe-131MXe-133Xe-133mXe-135Xe-135m2.22'2.100.02010.04540.0420.2470.432(2)(2)1.371.010.1430.1350.3.90.3170.095(2)(2)Xe-137Xe-1380.194l.18'.640.611(1)ORNL-4923, Radioactive Atoms-SulementI,M.S.Martin,November1973.(2)NEDO-12037, "SummaryofGammaandBetaEmittersandIntensity Data";M.E.""',".Meek,R.S.'Gilbert, January1970.(The.averageenergy..was computedfrom-'themaximumenergyusing.theICRPIIequation,.
notthe.1/3value..assumption usedinthisreference).
(3)NCRPReportNo.58,"AHandbookofRadioactivity Measurements Procedures";
1978(4)Theaverageenergyincludesconversion electrons.
fII"lQaI4"4~~~
fII"lQaI4"4~~~
LOCATIONResidencesDairyCowsMilkGoatsMeatAnimalsGardensSiteBoundaryDIRE(98O)SE(1300)E(88')ESE(115)E(97m)ENE(67)MILES1.42.67.91.81.80.41.8E-07b2.2E-08c1.3E-08c5.1E-08c1.0E-07c2.4E-06bDdD~/m-25.2E-09b7.0E-10c1.6E-10c17E09c3.5E-09c4.4E-08cDdTABLE3-1CriticalReceptorDispersionParsmetersaForGroundLevelandElevatedReleasesELEVATEDELEVATEDGROUNDe'4.02E-076.00E-082.57E-081.16E-072.53E-076.63E-06GROUNDeD/I/Dm~8.58E-091.64E-096.10K-103.54E-095.55E-096.35E-08a.ThesevalueswillbeusedindosecalculationsbeginninginApril1986butmayberevisedperiodicallytoaccountforchangesinlocationsoffarms,gardensorcriticalresidences.b.Valuesbasedon5yearannualmeteorologicaldata(C.T.Main,Rev.2)c.Valuesbasedon5yearaveragegrazingseasonmeteorologicaldata(C.T.MainRev.2)d.ValuearebasedonmostrestrictiveX/Qland-basedsector(ENE).(C.T.Main,Rev.2)e.Valuesarebasedonaverageannualmeteorologicaldatafortheyear1985.  
LOCATIONResidences DairyCowsMilkGoatsMeatAnimalsGardensSiteBoundaryDIRE(98O)SE(1300)E(88')ESE(115)E(97m)ENE(67)MILES1.42.67.91.81.80.41.8E-07b2.2E-08c1.3E-08c5.1E-08c1.0E-07c2.4E-06bDdD~/m-25.2E-09b7.0E-10c1.6E-10c17E09c3.5E-09c4.4E-08cDdTABLE3-1CriticalReceptorDispersion Parsmetersa ForGroundLevelandElevatedReleasesELEVATEDELEVATEDGROUNDe'4.02E-076.00E-082.57E-081.16E-072.53E-076.63E-06GROUNDeD/I/Dm~8.58E-091.64E-096.10K-103.54E-095.55E-096.35E-08a.Thesevalueswillbeusedindosecalculations beginning inApril1986butmayberevisedperiodically toaccountforchangesinlocations offarms,gardensorcriticalresidences.
~"q TABLE4-1DOSEFACTORSPORNOBLEGASESRadionuclidesKr-83mKr-85mKr-85Kr-87Kr-88Kr-89Kr-90Xe-131mXe-133mXe-133Xe-135mXe-135Xe-137Xe-138Xe-139Ar-41GammaAirDoseFactorMiBIZdpCi-yr1.93E+011.23E+031.72E+016.17E+031.52E+041.73E+041.63E+041.56E+023.27E+02353E+023.36E+031.92E+031.51E+039.21E+035.28E+039.30E+03BetaAirDoseFactorNimradmpCi-yr2.88E+021.97E+031.95E+031.03E+042.93E+031.06E+047.83E+031.11E+031.48E+031.05E+037.39E+022.46E+031.27E+044.75K+036.52E+043.28E+03*RegulatoryGuide1:109,"'CalculationofAnnualDosestoManFromRoutine.-.ReleasesofReactorEffluentsforthePurposeofEvaluatingCompliancewith10CPRPart50,Appends.xI,"datedOctober1977,page1.109-21.
b.Valuesbasedon5yearannualmeteorological data(C.T.Main,Rev.2)c.Valuesbasedon5yearaveragegrazingseasonmeteorological data(C.T.MainRev.2)d.Valuearebasedonmostrestrictive X/Qland-based sector(ENE).(C.T.Main,Rev.2)e.Valuesarebasedonaverageannualmeteorological datafortheyear1985.  
~"q TABLE4-1DOSEFACTORSPORNOBLEGASESRadionuclides Kr-83mKr-85mKr-85Kr-87Kr-88Kr-89Kr-90Xe-131mXe-133mXe-133Xe-135mXe-135Xe-137Xe-138Xe-139Ar-41GammaAirDoseFactorMiBIZdpCi-yr1.93E+011.23E+031.72E+016.17E+031.52E+041.73E+041.63E+041.56E+023.27E+02353E+023.36E+031.92E+031.51E+039.21E+035.28E+039.30E+03BetaAirDoseFactorNimradmpCi-yr2.88E+021.97E+031.95E+031.03E+042.93E+031.06E+047.83E+031.11E+031.48E+031.05E+037.39E+022.46E+031.27E+044.75K+036.52E+043.28E+03*Regulatory Guide1:109,"'Calculation ofAnnualDosestoManFromRoutine.-.ReleasesofReactorEffluents forthePurposeofEvaluating Compliance with10CPRPart50,Appends.x I,"datedOctober1977,page1.109-21.
4p$ell~"Ib$IIh eTABLE4-2RVALUES-COW'SMILK-INFANT2md~rem/ruCi-secNUCLIDEH3"Cr51Mn54Fe55Fe59Co58Co60Zn65Sr80Sr90Zr95I131I133CH134Cs136Cs137Ba140Ce141em~rem/ruCi/mT.BODY2.40803GI-TRACT2.40E031.458077.218072.888071.11E085.268091.708081.798105.588026.928087.918063.598091.038092.378095.948061.448036.918068.748072.888071.128089.638091.22808Se758083.92E055.628074.578069'5E074.19E071.048082.838076.30E067.468042.178064.548067.36806BONE8.438071.05E083.32E095.948097.018103.238031.348091.85E071.908109.37E082.858101.158082.00804LIVER2.408032.008075.448071..158074.71E071.148107.878021.57E092.708073.558102.768093.348101.158051.22804KIDNEY2.40E031.068044.44E065.53E09Be48E021.848093'78079.14E091.10E098.968092.74E043.76E03THYROID2.408034.878045.178ll4.91809LUNG2.408034.478042.66807)5.418073.758092.258.083.638097.03804  
4p$ell~"Ib$IIh eTABLE4-2RVALUES-COW'SMILK-INFANT2md~rem/ruCi-secNUCLIDEH3"Cr51Mn54Fe55Fe59Co58Co60Zn65Sr80Sr90Zr95I131I133CH134Cs136Cs137Ba140Ce141em~rem/ruCi/mT.BODY2.40803GI-TRACT2.40E031.458077.218072.888071.11E085.268091.708081.798105.588026.928087.918063.598091.038092.378095.948061.448036.918068.748072.888071.128089.638091.22808Se758083.92E055.628074.578069'5E074.19E071.048082.838076.30E067.468042.178064.548067.36806BONE8.438071.05E083.32E095.948097.018103.238031.348091.85E071.908109.37E082.858101.158082.00804LIVER2.408032.008075.448071..158074.71E071.148107.878021.57E092.708073.558102.768093.348101.158051.22804KIDNEY2.40E031.068044.44E065.53E09Be48E021.848093'78079.14E091.10E098.968092.74E043.76E03THYROID2.408034.878045.178ll4.91809LUNG2.408034.478042.66807)5.418073.758092.258.083.638097.03804  
~SX44IJ~~gtp ThBLE4-3RVhLUES-COM'SMILK-CHILD2m~~remjrQCi-secNUCLIDEH3>Cr51Mn54Pe55Pe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136CQ137Ba140Ce141~m~remlruCi/m3T.BODY1.58E034.71B042.87E061.15E074.52E071.77E076.81S074.10E098.93E071.63B103.56B023.66E084.11S064.09E098.53E082.52B093.27E067.47B02CI-TRhCT1.58E032.50S069.04E066.85E069.45B073.37E071.28E081.16S091.21S088.68E084.17E055.73E074.38E061.05B084.63E071.07B082.84B076.28E06BONE6.97E075.61E072.47E093.13E096.44$101.82S036.40E088.78E061.18E104.80S081.79E105.60E071.01E04LIVER1.58E031.08B073.07E079.08E075.77S062.31E076.59E094.00E026.44E081.09E071.94E101.32E091.71E104.91E045.03E03KIDNEY1.58E037.14E033.02S064.15E095.72E021.06E091.81E076.01E097.07S085.57B091.60E042.21E03THYROID1.58E032.61E042.13Ell2.02E09LUHC1.58S03)<4.77E042.09E072.63E072.16E091.05E082.00S092.93E04 Ir,"8)\~ff4/!,gtp4 TABLE4-4RVALUES-COW'SMILK-TEEN2m~~rcimleuCi-secNUCLIDE83>Cc'1Mn54Fe55Pe59Co5&Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136Cs137Ba140Ce141*miamiuCi/m3T.BODY1.00E2.31E0304&.10E3.35E2.04E3.62E9.42E06070907091.70E021.98E1.87E5.60E5.62B3.44E1.5&E0806090809063.14E021.43B064.59E062.1&E07GI-TRACT1.00E033.88E061.4&E078.52B061.34E085.21E071.94E081.85E091.50E081.07E095.70E057.31E074.64B061.50E086.73E071.40E083.5&E077.83E06BONE,1.5&E032.7&E072.42E071.26E091.26E093.81E107.83E022.64B083.61E065.12E092.13E087.42E092.32E074.10E03LIVER1.00E031.20E061.97E075.65E073.78E061.49E074.3&E092.47E023.69B086.13E061.21E108.37E089.87E092.84E042.74E03KIDNEY1.00E035.06E032.15E062.&OE093.63E026.36E081~0&E073.83E094.55E083.36E099.65E031.29E03THYROID1.00E031.2&E041.0&Ell8.56E08LUNG1.00E033.30E041.25E071.7&E071.46E097.1&E071.30B091.91E04 llIplx''g5.iJ TABLE4-5RVALUES-COM'SMILK-ADULT2md~rem/uci-secNUCLIDEH3~Cr51Mn54Pe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134CQ136Cs137Ba140Ce141>m~rsmlruci/mT.BODY7.69E021.32E048.25E052.52E061.25E075.03B061.93E071.18S091.97B076.62E099.72E011.19E081.05E065.74E093.55E083.65E098.43E051.71E02GI-TRACT"7.69S023.32E061.32E076.21E061.09B084.56B071.65B081.65E091.10E087.80S084.55E055.49E073.09E061.23E085.60E071.08E082.65E075.78E06SONS1.57E071.39E078.21E086.85E082.70E104.48E021.45E081.98E062.95E091.25E084.09E091.29E072.24E03LIVER7.69E024.32E061.08E073.26E072.24E068.77E072.81E091.44B022.08E083.44E067.02E094.93E085.59E091.62E041.51E03KIDNEY7.69E022.91S031.29E061.75E092.25E023.57E086.01E062.27E092.74E081.90E095.49E037.02E02THYROID7.69E027.90E036.82E105.06B08LUNG7.69E021.75E046.04E069.10B067.54E083.76E076.31E089.25S03  
~SX44IJ~~gtp ThBLE4-3RVhLUES-COM'SMILK-CHILD2m~~remjrQCi-secNUCLIDEH3>Cr51Mn54Pe55Pe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136CQ137Ba140Ce141~m~remlruCi/m3T.BODY1.58E034.71B042.87E061.15E074.52E071.77E076.81S074.10E098.93E071.63B103.56B023.66E084.11S064.09E098.53E082.52B093.27E067.47B02CI-TRhCT1.58E032.50S069.04E066.85E069.45B073.37E071.28E081.16S091.21S088.68E084.17E055.73E074.38E061.05B084.63E071.07B082.84B076.28E06BONE6.97E075.61E072.47E093.13E096.44$101.82S036.40E088.78E061.18E104.80S081.79E105.60E071.01E04LIVER1.58E031.08B073.07E079.08E075.77S062.31E076.59E094.00E026.44E081.09E071.94E101.32E091.71E104.91E045.03E03KIDNEY1.58E037.14E033.02S064.15E095.72E021.06E091.81E076.01E097.07S085.57B091.60E042.21E03THYROID1.58E032.61E042.13Ell2.02E09LUHC1.58S03)<4.77E042.09E072.63E072.16E091.05E082.00S092.93E04 Ir,"8)\~ff4/!,gtp4 TABLE4-4RVALUES-COW'SMILK-TEEN2m~~rcimleuCi-secNUCLIDE83>Cc'1Mn54Fe55Pe59Co5&Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136Cs137Ba140Ce141*miamiuCi/m3T.BODY1.00E2.31E0304&.10E3.35E2.04E3.62E9.42E06070907091.70E021.98E1.87E5.60E5.62B3.44E1.5&E0806090809063.14E021.43B064.59E062.1&E07GI-TRACT1.00E033.88E061.4&E078.52B061.34E085.21E071.94E081.85E091.50E081.07E095.70E057.31E074.64B061.50E086.73E071.40E083.5&E077.83E06BONE,1.5&E032.7&E072.42E071.26E091.26E093.81E107.83E022.64B083.61E065.12E092.13E087.42E092.32E074.10E03LIVER1.00E031.20E061.97E075.65E073.78E061.49E074.3&E092.47E023.69B086.13E061.21E108.37E089.87E092.84E042.74E03KIDNEY1.00E035.06E032.15E062.&OE093.63E026.36E081~0&E073.83E094.55E083.36E099.65E031.29E03THYROID1.00E031.2&E041.0&Ell8.56E08LUNG1.00E033.30E041.25E071.7&E071.46E097.1&E071.30B091.91E04 llIplx''g5.iJ TABLE4-5RVALUES-COM'SMILK-ADULT2md~rem/uci-secNUCLIDEH3~Cr51Mn54Pe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134CQ136Cs137Ba140Ce141>m~rsmlruci/mT.BODY7.69E021.32E048.25E052.52E061.25E075.03B061.93E071.18S091.97B076.62E099.72E011.19E081.05E065.74E093.55E083.65E098.43E051.71E02GI-TRACT"7.69S023.32E061.32E076.21E061.09B084.56B071.65B081.65E091.10E087.80S084.55E055.49E073.09E061.23E085.60E071.08E082.65E075.78E06SONS1.57E071.39E078.21E086.85E082.70E104.48E021.45E081.98E062.95E091.25E084.09E091.29E072.24E03LIVER7.69E024.32E061.08E073.26E072.24E068.77E072.81E091.44B022.08E083.44E067.02E094.93E085.59E091.62E041.51E03KIDNEY7.69E022.91S031.29E061.75E092.25E023.57E086.01E062.27E092.74E081.90E095.49E037.02E02THYROID7.69E027.90E036.82E105.06B08LUNG7.69E021.75E046.04E069.10B067.54E083.76E076.31E089.25S03  
~el'V~,J/
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TABLE4-6RVALUES-GOAT'SHILK-INFANT2mm~eemleuCi-secNUCLIDSH3~Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136CQ137Ba140Ce141em~eemleuCi/m3T.BODY4.90E038.95B035.45E051.89S059.37E053.45B061.34E07&.31S083.58E083.57E106.70E018.31E089.49E061.08E103.09E097.10S09e7.13E051.72E02GI-TRACT4.90B032.61E058.83E058.98E041.14B063.45E061.35E071.16E092.57E081.84E094.70E046.74E075.48E062.89E081.26E083.13E083.40E067.57E05BONE1.10E061.36E063.99E081.25E101.47E113.88E.021.60E092.23E075.71E102.81E098.55E101.38E072.40E03LIVER4.90S032.40E067.08E052.38E061.38E065.65S061.37E099.45EOl1.89E093.24E071.07E118.27E091.00E111.38E041.46E03KIDNEY4.90E031.28E035.33S056.63E081.02E022.21E093.81E072.74E103.30B092.69E103.29S034.52E02THYROID4.90E035.84B036.21Ell5.89S09LUNG4.90E031.14E043.46B057.03B051.12E106.74E081.09E108.50E03 qlI04i$:~I'<~rLOFTlg1I~N"'+i'51 TABLE4-7RVALUES-GOAT'SMILK-CHILD2m~~ramlruCi-secNUCLIDEH3"Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136Cs137Ba140Ce141*m~rrmjruCi/mT.BODY3.23E035.65E033.44E051.49E055.88B052.12E068.17E064.92S081.87B083.43E104.27E014.39E084.93E061.23E102.56S097.57E093.92E058.97E01GI-TRACT3.23E033.00B051.08E068.91E041.23E064.04E061.53E071.39E082.54B081.82E095.01S046.88E075.25B063.14E081.39E083.21B083.41E06:7.54E05BONE9.06E057.29E052.97B086.56S091.35Ell2.18S027.68E081.05E073.55E101.44E095.36E106.72E061.21E03LIVER3.23E03i1.29E064.81E051.18E066.92E052.77E067.91E084.80E017.72E081.30E075.82E103.96E095.13E105.89E036.04E02KIDNEY3.23E~038.57E023.62E054.98E086.87E011.27S092.17E071.80E102.11E091.67E101.92E032.65E02THYROID3.23E033.14E032.55Ell2.42E09LUNG3.23E035.73E032.72E053.42E056.47E093.14E086.01E093.51S03 V&IkP*1yEr1)~g ThBLE4-8RVhLUES-GOhT'SMILK-TEEN2m~~rmm/uCi-seeNUCLIDBH3"Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134CH136Cs137BR140Ce141*m~ram/uCi/m3T.BODY2.04E032.77S031.71E055.97B042.83E051.04B064.02E062.45E087.59S071.98B102.04E012.38B082.24S061.68E101.69S091.03E101.80E053.77EOlGI-TRhCT2.04E034.66B051.77E061.11E051.74B066.25E062.32E072.22S083.16E082.25E096.84E048.77E075.57E064.50E082.02E084.21E084.30E069.39E05BONE3.61E053.14E051.51E082.65E098.81B109.40EOl3.17B084.34B061.54E106.38E082.22E102.97E064.92E02LIVER2.04E038.64E052.56E05KIDNEY2.04E036.07E022.58E052.97E014.43E087.36E063.62E102.51B092.96E103.41E033.28E024.36EOl7.63E081.29E071.15E101.37E091.01E101.16E031.55E027.34E054.63E051.78E065.25E083.36E08THYROID2.04E031.54E031.29Ell1.03E09LUNG2.04E033.95E031.62E05I42.31E054.39E092.15E083.91E092.30E03 II(1JhJ0 TABLE4-9RVALUES-GOAT'SMILK-ADULT2mm~eemluci-secNUCLIDEH3"Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136Cs137Ba140Ce141em~rem/uCi/mT.BODY1.57E031.59E039.89E043.28E041.62E056.03E052.32E061.42E084.13E071.39E101.17EOl1.43E081.26B061.72E101.06E091.10E101.01E052.06E01GI-TRACT1.57E033.99E051.59E068.07E04'1.41E065.46E061.98B071.97E082.31E081.64E095.46E046.59E073.71B063.69E081.68E083.25E083.18E066.94B05BONEe2.04E051.80E059.85B071.44E095.67E105.37E.Ol1.74E082.37E068.85E093.75E081.25E101.54E062.68E02LIVER1.57E03e5.19E051.41E054.23E052.69E051.05E063.14E081.72E012.50E084.13E062.11E101.48E091.68E101.94E031.81E02KIDNEY1.57E033.49E021.54E052.10E082.70EOl4.28E087.21E066.82E098.23E085.70E096.59E028.43EOlTHYROID1.57E039.48E028.18E106.07E08LUNG1.57E032.11E037.85E04I1.18E052.26E091.13E081.89E091.11E03 Ptr1Ci TABLB4-10RVALUES-MEAT-CHILD2m~~remlruCi-secNUCLIDEH3<Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136Cs137Ba140Ce141em~rem/ruCi/m3T.BODY2.36B024.07E031.09E064.74B071.42E082.39B071.09E083.72B08.6.55E061.52E092.48E054.64E061.55B-011.67E081.35B071.04B081.22B067.57E02GI-TRACT2.36B022.16E053.45B062.84B072.97B084.56E072.05E081.05E088.87E068.08B072.91E087.29E051.66E-Ol4.26E067.34B054.43B061.06B076.36B06BONE2.89B081.76B082.25E082.29$086.00E091.27B068.14B063.32B-014.81B087.60E067.39B08gelOE071.02B04LIVER2.36E024.11E061.53E082.85E087.82E063.70E075.99E082.79E058.19E064.11B-017.90B082.09E077.07B081.84E045.10E03KIDNEY2.36E026.17E021.15E063.77E083.99E051.34B076.85B-012.45E081.11E072.30E085'8E032.24E03THYROID2.36B022.26E032.71B097.63E-01LUNG2.36E024.12B038.66B07)'.26E078.78B071.66E068.29E071.10E04 J'WPwp'',tg.yl'Ip4 TABLE4-11RVALUES-MBAT-TEEN2m~~remlruCi-secNUCLIDECr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136CB137Ba140Ce141em~rem/ruCi/m3T.BODY1.95E022.61E037.12E052.49E078.95E071.54E077.03E072.43B083.47E061.15E091.55E053.30E069.25E-022.98E081.16B071.86B087.33E054.14E02GI-TRACT1.95E024.39E057.37E064.62E075.48B089.22E074.06E082.20E081.44E071.30E085.20E081.22E062.30E-017.99E061.40E067.59E061.75E071.04E07BONE1.50E089.93E071.50E081.21E084.64E097.15E054.39E061.79E-012.73E084.41E064.01E081.14E075.43E03LIVER1.95E023.59E061.07E082.32E086.69E063.12E075.20E082.25E056.14B063.03E-016.42E081.73E075.34B081.39E043.63E03KIDNEY1.95E025.72E021.07E063.33E083.31E051.06E075.32E-012.04E089.44E061.82E084.72E031.71E03THYROID1.95E021.45E031.79E094.23E01LUNG1.95E023.73E036.77E0747.31E077.78E071.49E067.06E079'7E03 tCAr4r TABLE4-12RVALUES-MEAT-ADULT2md~rem/ruCi-secNUCLIDEH3~Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133CH134Cs136Cs137Ba140Ce141*m~remlruCi/mT.BODY3.27E023.26B038.98E052.98E071.12E081.95E078.87B073.06E084.12E061.76E091.94E054.33E061.13E-Ol6.68E081.61E074.33E089.01B054.96E02GI-TRACT3.27B028.21E051.44E077.34B079.73B081.76E087.56E084.27B082.30E072.07B089.07E081.99E063.34E-011.43E072.53E061.28B072.83E071.67B07BONE1.85E081.24E082.13E081.43E087.17E09'.92E055.28E062.14E-013.43E085.65E064.83E081.38K076.47E03LIVER3.27E024.71E061.28E082.92E088.68E064.02E6.78E07082.86E057.55E063.72E-018.15K082.23E076.61E081.73E044.38E03KIDNEY3.27B027.19E021.40E064.53E084.49E051.29E076.49B-012.64E081.24E072.24E085.87E032.03E03THYROID3.27E021.95K032.48E095.46E01LUNG3.27E024.33$037.14B07].8.16E078.78E071.70E067.46E079.89E03 AT ThBLE4-13RVhLUES-VSGSThTION-CHILD2md~rem/ruCi-secNUCLIDEH3*Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Se90Zr95I131I133Cs134Cs136Cs137Ba140Ce141em~rem/ruCi/m3T.BODY4.048031.168051.73E081.258083.17E081.928081.118091.70S091.03E093.498ll7.448058.168071.678065.408091.438083.528091.618074.75E04GI-TRhCT4.048036.15E065.44E087.50E076.628083.668082.088094.818081.408091.868108.718081.288071.788061.388087.77E061.50E081.408083.99808BONE7.638083.938081.03E093.62810'.388123.808061.438083.578061.568108.048072.488102.768086.42E05LIVER4.048036.498084.05E086.36E086.278063.768082.748098.358051.44E084'28062.568102.218082.398102.428053.20E05KIDNEY4.048031.768041.82E081.738091.208062.368087.368067.93E091.18E087.78E097.878041.40E05THYROID4.048036.448044.758108.21808LUNG4.048031.188052.29808141.848082.848091.768072.808091.44805 F4-0c4~'r.elf/~'~
TABLE4-6RVALUES-GOAT'SHILK-INFANT2mm~eemleuCi-secNUCLIDSH3~Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136CQ137Ba140Ce141em~eemleuCi/m3T.BODY4.90E038.95B035.45E051.89S059.37E053.45B061.34E07&.31S083.58E083.57E106.70E018.31E089.49E061.08E103.09E097.10S09e7.13E051.72E02GI-TRACT4.90B032.61E058.83E058.98E041.14B063.45E061.35E071.16E092.57E081.84E094.70E046.74E075.48E062.89E081.26E083.13E083.40E067.57E05BONE1.10E061.36E063.99E081.25E101.47E113.88E.021.60E092.23E075.71E102.81E098.55E101.38E072.40E03LIVER4.90S032.40E067.08E052.38E061.38E065.65S061.37E099.45EOl1.89E093.24E071.07E118.27E091.00E111.38E041.46E03KIDNEY4.90E031.28E035.33S056.63E081.02E022.21E093.81E072.74E103.30B092.69E103.29S034.52E02THYROID4.90E035.84B036.21Ell5.89S09LUNG4.90E031.14E043.46B057.03B051.12E106.74E081.09E108.50E03 qlI04i$:~I'<~rLOFTlg1I~N"'+i'51 TABLE4-7RVALUES-GOAT'SMILK-CHILD2m~~ramlruCi-secNUCLIDEH3"Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136Cs137Ba140Ce141*m~rrmjruCi/mT.BODY3.23E035.65E033.44E051.49E055.88B052.12E068.17E064.92S081.87B083.43E104.27E014.39E084.93E061.23E102.56S097.57E093.92E058.97E01GI-TRACT3.23E033.00B051.08E068.91E041.23E064.04E061.53E071.39E082.54B081.82E095.01S046.88E075.25B063.14E081.39E083.21B083.41E06:7.54E05BONE9.06E057.29E052.97B086.56S091.35Ell2.18S027.68E081.05E073.55E101.44E095.36E106.72E061.21E03LIVER3.23E03i1.29E064.81E051.18E066.92E052.77E067.91E084.80E017.72E081.30E075.82E103.96E095.13E105.89E036.04E02KIDNEY3.23E~038.57E023.62E054.98E086.87E011.27S092.17E071.80E102.11E091.67E101.92E032.65E02THYROID3.23E033.14E032.55Ell2.42E09LUNG3.23E035.73E032.72E053.42E056.47E093.14E086.01E093.51S03 V&IkP*1yEr1)~g ThBLE4-8RVhLUES-GOhT'SMILK-TEEN2m~~rmm/uCi-seeNUCLIDBH3"Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134CH136Cs137BR140Ce141*m~ram/uCi/m3T.BODY2.04E032.77S031.71E055.97B042.83E051.04B064.02E062.45E087.59S071.98B102.04E012.38B082.24S061.68E101.69S091.03E101.80E053.77EOlGI-TRhCT2.04E034.66B051.77E061.11E051.74B066.25E062.32E072.22S083.16E082.25E096.84E048.77E075.57E064.50E082.02E084.21E084.30E069.39E05BONE3.61E053.14E051.51E082.65E098.81B109.40EOl3.17B084.34B061.54E106.38E082.22E102.97E064.92E02LIVER2.04E038.64E052.56E05KIDNEY2.04E036.07E022.58E052.97E014.43E087.36E063.62E102.51B092.96E103.41E033.28E024.36EOl7.63E081.29E071.15E101.37E091.01E101.16E031.55E027.34E054.63E051.78E065.25E083.36E08THYROID2.04E031.54E031.29Ell1.03E09LUNG2.04E033.95E031.62E05I42.31E054.39E092.15E083.91E092.30E03 II(1JhJ0 TABLE4-9RVALUES-GOAT'SMILK-ADULT2mm~eemluci-secNUCLIDEH3"Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136Cs137Ba140Ce141em~rem/uCi/mT.BODY1.57E031.59E039.89E043.28E041.62E056.03E052.32E061.42E084.13E071.39E101.17EOl1.43E081.26B061.72E101.06E091.10E101.01E052.06E01GI-TRACT1.57E033.99E051.59E068.07E04'1.41E065.46E061.98B071.97E082.31E081.64E095.46E046.59E073.71B063.69E081.68E083.25E083.18E066.94B05BONEe2.04E051.80E059.85B071.44E095.67E105.37E.Ol1.74E082.37E068.85E093.75E081.25E101.54E062.68E02LIVER1.57E03e5.19E051.41E054.23E052.69E051.05E063.14E081.72E012.50E084.13E062.11E101.48E091.68E101.94E031.81E02KIDNEY1.57E033.49E021.54E052.10E082.70EOl4.28E087.21E066.82E098.23E085.70E096.59E028.43EOlTHYROID1.57E039.48E028.18E106.07E08LUNG1.57E032.11E037.85E04I1.18E052.26E091.13E081.89E091.11E03 Ptr1Ci TABLB4-10RVALUES-MEAT-CHILD2m~~remlruCi-secNUCLIDEH3<Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136Cs137Ba140Ce141em~rem/ruCi/m3T.BODY2.36B024.07E031.09E064.74B071.42E082.39B071.09E083.72B08.6.55E061.52E092.48E054.64E061.55B-011.67E081.35B071.04B081.22B067.57E02GI-TRACT2.36B022.16E053.45B062.84B072.97B084.56E072.05E081.05E088.87E068.08B072.91E087.29E051.66E-Ol4.26E067.34B054.43B061.06B076.36B06BONE2.89B081.76B082.25E082.29$086.00E091.27B068.14B063.32B-014.81B087.60E067.39B08gelOE071.02B04LIVER2.36E024.11E061.53E082.85E087.82E063.70E075.99E082.79E058.19E064.11B-017.90B082.09E077.07B081.84E045.10E03KIDNEY2.36E026.17E021.15E063.77E083.99E051.34B076.85B-012.45E081.11E072.30E085'8E032.24E03THYROID2.36B022.26E032.71B097.63E-01LUNG2.36E024.12B038.66B07)'.26E078.78B071.66E068.29E071.10E04 J'WPwp'',tg.yl'Ip4 TABLE4-11RVALUES-MBAT-TEEN2m~~remlruCi-secNUCLIDECr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136CB137Ba140Ce141em~rem/ruCi/m3T.BODY1.95E022.61E037.12E052.49E078.95E071.54E077.03E072.43B083.47E061.15E091.55E053.30E069.25E-022.98E081.16B071.86B087.33E054.14E02GI-TRACT1.95E024.39E057.37E064.62E075.48B089.22E074.06E082.20E081.44E071.30E085.20E081.22E062.30E-017.99E061.40E067.59E061.75E071.04E07BONE1.50E089.93E071.50E081.21E084.64E097.15E054.39E061.79E-012.73E084.41E064.01E081.14E075.43E03LIVER1.95E023.59E061.07E082.32E086.69E063.12E075.20E082.25E056.14B063.03E-016.42E081.73E075.34B081.39E043.63E03KIDNEY1.95E025.72E021.07E063.33E083.31E051.06E075.32E-012.04E089.44E061.82E084.72E031.71E03THYROID1.95E021.45E031.79E094.23E01LUNG1.95E023.73E036.77E0747.31E077.78E071.49E067.06E079'7E03 tCAr4r TABLE4-12RVALUES-MEAT-ADULT2md~rem/ruCi-secNUCLIDEH3~Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133CH134Cs136Cs137Ba140Ce141*m~remlruCi/mT.BODY3.27E023.26B038.98E052.98E071.12E081.95E078.87B073.06E084.12E061.76E091.94E054.33E061.13E-Ol6.68E081.61E074.33E089.01B054.96E02GI-TRACT3.27B028.21E051.44E077.34B079.73B081.76E087.56E084.27B082.30E072.07B089.07E081.99E063.34E-011.43E072.53E061.28B072.83E071.67B07BONE1.85E081.24E082.13E081.43E087.17E09'.92E055.28E062.14E-013.43E085.65E064.83E081.38K076.47E03LIVER3.27E024.71E061.28E082.92E088.68E064.02E6.78E07082.86E057.55E063.72E-018.15K082.23E076.61E081.73E044.38E03KIDNEY3.27B027.19E021.40E064.53E084.49E051.29E076.49B-012.64E081.24E072.24E085.87E032.03E03THYROID3.27E021.95K032.48E095.46E01LUNG3.27E024.33$037.14B07].8.16E078.78E071.70E067.46E079.89E03 AT ThBLE4-13RVhLUES-VSGSThTION
eThBLE4-14RVhLUES-VEGEThTION-TBEN2.m~~eemleuci-secNUCLIDEH3>Cr51Hn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134CQ136Cs137Ba140Ce141*deem/euCi/m3T.BODY2.61E036.11E048.79E075.13E071.60E089.79E075.57E088.68B084.36E082.05Ell3.68E055.77E071.01E067.54E091.13E084.90B098.88E062.12E04GI-TRhCT2.61E031.03E079.89E089.53B079.78E085.85E083.22E097.88E081.81E092.33E101.23E092.13B072.51E062.02E081.35B072.00B082.12E085.29E08HONE3.10E081.77E085.36E081.52E108.32Ell1.69E.067.68E071.96E066.96E094.28E071.06E101.38E082.77E05LIVER2.61E034.43E082.20E084.14E084.25E072.47E081.86E095.35B051.07E083.32E061.62E101.68E081.41E101.69E051.85E05KIDNEY2.61E031.34E041.32E081.19E097.86E061.85E085.83E065.16E099.16E074.78E095.72E048.70E04THYROID2.61E033.39E043.14E104.64E08LUNG2.61E038.72E041.40B08IE1.30E081.97E091.44E071.86E091.14E05 S>>I'rIrVt"iP1tS"4kt''AaJ+lyt0 eTABLE4-15RVALUES-VEGETATION-ADULT2m~~remlruCi-secNUCLIDEN3<Cr51Mn54Fe55Pe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134CB136Cs137Ba140Ce141em~rem/uCi/m3T.BODY2.28E03GI-TRACT2.28S033.22S071.12E086.71E073.67E085.77S082.87E081.64Ell2.51S056.61E071.12S068.83E091.19E085.94E098.40E061.48E047.91E079.75S086.07E083.12$098.04E081.60E091.93S101.17E093.04E073.30E061.89E081.88E071.76E082.64E084.99E084.60E041.16E075.83E079.36E08BONE2.00E081.24E084.01E081.08E106.70Ell1.16E068.07E072.11E064.54E094.19E076.63E091..28E081.93E05LIVER2.28E033.05S081.38S082.93E082.99E071.66E081.28E093.71E051.15E083.67E061.08S101.66E089.07E091.61E051.$1E05KIDNEY2.28E031.01E049.09E078.54E085.82E051.98E086.40E063.49E099.21E073.08E095.47E046.07E04THYROID2.288032.75E043.78E105.39E08LUNG2.28E036.10E047.69E07<8.17E071.16E091.26E071.02E099.22E04  
-CHILD2md~rem/ruCi-secNUCLIDEH3*Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Se90Zr95I131I133Cs134Cs136Cs137Ba140Ce141em~rem/ruCi/m3T.BODY4.048031.168051.73E081.258083.17E081.928081.118091.70S091.03E093.498ll7.448058.168071.678065.408091.438083.528091.618074.75E04GI-TRhCT4.048036.15E065.44E087.50E076.628083.668082.088094.818081.408091.868108.718081.288071.788061.388087.77E061.50E081.408083.99808BONE7.638083.938081.03E093.62810'.388123.808061.438083.578061.568108.048072.488102.768086.42E05LIVER4.048036.498084.05E086.36E086.278063.768082.748098.358051.44E084'28062.568102.218082.398102.428053.20E05KIDNEY4.048031.768041.82E081.738091.208062.368087.368067.93E091.18E087.78E097.878041.40E05THYROID4.048036.448044.758108.21808LUNG4.048031.188052.29808141.848082.848091.768072.808091.44805 F4-0c4~'r.elf/~'~
~Otktl4!a TABLE.4-16RVALUES-INHALATION-INFANTI~ram/ruCi/m3NUCLIDEH3Cr51Mn54Pe55Fe59CoSsCo60Zn65Sr89Sr90Zr95I131I133CQ134Cs136Cs137Ba140Ce141T.BODY6.468028.938014.988033.338039.468031.82E031.188043.108041.148042.598062.03804I1.968045.598037.448045.288044.548042.898031.99803GI-TRACT6.468023.568027.058031.098032.478041.118043.188045.138046.398041.318052.178041.068032.158031.338031.438031.338033.83E042.15804BONE1.978041.358041.938043.978054.OSSO71.158053.798041.328043.968054.828045.4SSOS5.59E042.77804LIVER6.468022.538041.178042.368041.228038.018036.258042.788044.438041.92E047.02E051.348056.118055.598011.66804KIDNEY6.46E021.328014.98E033.248043.10E045.178042.248041.908055.638041.728051.348Ol5.24803THYROID6.468025.758011.488073.55806LUNG6.468021.288049.98E058.698041.018067.768054.508066.468052.038061.128071.758067.958041.178047.128041.59806P5.16805  
eThBLE4-14RVhLUES-VEGEThTION
%W\4"pCC>4r ThBLB.4-17RVhLUES-INHhLhTION-CHILDmasm/ruCi/m3NUCLIDBH3Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133CQ134CQ136CQ137Ba140Ce141T.BODY1.128031.548029.508037.778031.678043.168032.268047.028041.728046.438063.698042.728047.688032.248051.168051.288054.328032.89803CI-TRhCT1.128031.088032.298042.878037.068043.438049.618041.638041.678053.438056.108042.848035.478033.848034.178033.618031.028055.65804BONE4.748042.078044.258045.998051.018081.908054.808041.668046.50E056.508049.058057.398043.92E04LIVER1.128034.298042.528043.348041.778031.318041.138054.178044.808042.038041.01S061.718058.248056.478Ol1.95804KIDNEY1.128032.43E011.008047.138045.958047.878043.378043.308059.538042.828052.118Ol8.53803THYROID1.128038.538011.628073.84806LUNG1.128031.708041.57S061.118051.278061.10E067.068069.948052.158061.478072.238061.218051.458041.048051748061*5.43805 V4'>>I~<<kA~I<<ff,*Ifl>>'>>-<<ArI<<4>>,~'>>>>N>>I7g>>
-TBEN2.m~~eemleuci-secNUCLIDEH3>Cr51Hn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134CQ136Cs137Ba140Ce141*deem/euCi/m3T.BODY2.61E036.11E048.79E075.13E071.60E089.79E075.57E088.68B084.36E082.05Ell3.68E055.77E071.01E067.54E091.13E084.90B098.88E062.12E04GI-TRhCT2.61E031.03E079.89E089.53B079.78E085.85E083.22E097.88E081.81E092.33E101.23E092.13B072.51E062.02E081.35B072.00B082.12E085.29E08HONE3.10E081.77E085.36E081.52E108.32Ell1.69E.067.68E071.96E066.96E094.28E071.06E101.38E082.77E05LIVER2.61E034.43E082.20E084.14E084.25E072.47E081.86E095.35B051.07E083.32E061.62E101.68E081.41E101.69E051.85E05KIDNEY2.61E031.34E041.32E081.19E097.86E061.85E085.83E065.16E099.16E074.78E095.72E048.70E04THYROID2.61E033.39E043.14E104.64E08LUNG2.61E038.72E041.40B08IE1.30E081.97E091.44E071.86E091.14E05 S>>I'rIrVt"iP1tS"4kt''AaJ+lyt0 eTABLE4-15RVALUES-VEGETATION
TABLE4-18RVALUES-INHALATION-TEENm~mamimuCi/m3NUCLIDEH3Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133CH134Cs136Cs137Ba140Ce141T.BODY1.27E031.358028.398035.548031.438042.778031.98E046.238041.25E046.678063.158042.648046.218035.488051.378053.118053.518032.16803GI-TRACT1.278033.008036.678046.398031.788059.518042.598054.668043.718057.648051.498056.488031.038049.758031.098048.478032.288051.26805BONE3.348041.598043.858044.348051.08E081.458053.548041.218045.028055.148046.698055.468042.84804LIVER1.27E035.108042.388043.698042.078031.518041.338054.588044.908042.05E041.138061.938058.478056.698011.89804KIOMEY1.278033.078Ol1.278048.63E046.738048.39E043.59E043.75E051.108053.048052.248Ol8.87803THYROID1.278037.498011.468072.92806LUNG1.27E032.098041.988061.24805'.538061.348068.718061.248062.41E061.65E07=-2.688061.468051.778041.218052.038066.13E05 k~I+vs.f1 TABLE4-19RVALUES-INHALATION-ADULTm~rem/ruC1/m,3eNUCLIDEH3Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136Cs137Ba140Ce141T.BODY1.268039.998Ol6.29E033.948031.058042.078031.488044.658048.718036.09E062.328042.058044.518037.278051.10804GI-TRACT1.268033.32E037.72E046.038031.888051.068052.848055.348043.498057.218051.508056.278038.878031.048041.17E042.568031.53E032.188051.20E054.27E058.39803BONE2.468041.17804.3.248043.048059.91E071.078052.528048.638033.728053.908044.788053.908041.99804LIVER1.268033.958041.708042.778041.588031.158041.03E053.44E043.578041.488048.478051.468056.208054.908Ol1.35804KIDNEY1.268032.288019e838036e898045.418046.12E042.588042e878058.558042.22E051.678Ol6.25E03THYROID1.26E035.948Ol1.198072.15806LUNG1.268031.448041.4087.2181.01806pgc069.758041.208047.518041.278063.618059.278055.968068.638051.408069.59E061.77806 lpga TABLE4-20RVALUES-GROUND-ALLAGEGROUPS2M~modem/e>>Ci/secNUCLIDE1.BODYCr51Mn54Fe55Fe59Co58Co60Zn65Sr89Zr95I.131I133~.Cs134Cs136Cs137"Ba140'Ce141,I135Ba/La140Nb95Sb1254.66E061.34E092.75E083.79E082.15E107.49E082.23E042.49E081.72E072.47E066.82E091.49E081.03E102.05E071.36E07LaterLaterLaterLater PYf4401etr"'g'i,~
-ADULT2m~~remlruCi-secNUCLIDEN3<Cr51Mn54Fe55Pe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134CB136Cs137Ba140Ce141em~rem/uCi/m3T.BODY2.28E03GI-TRACT2.28S033.22S071.12E086.71E073.67E085.77S082.87E081.64Ell2.51S056.61E071.12S068.83E091.19E085.94E098.40E061.48E047.91E079.75S086.07E083.12$098.04E081.60E091.93S101.17E093.04E073.30E061.89E081.88E071.76E082.64E084.99E084.60E041.16E075.83E079.36E08BONE2.00E081.24E084.01E081.08E106.70Ell1.16E068.07E072.11E064.54E094.19E076.63E091..28E081.93E05LIVER2.28E033.05S081.38S082.93E082.99E071.66E081.28E093.71E051.15E083.67E061.08S101.66E089.07E091.61E051.$1E05KIDNEY2.28E031.01E049.09E078.54E085.82E051.98E086.40E063.49E099.21E073.08E095.47E046.07E04THYROID2.288032.75E043.78E105.39E08LUNG2.28E036.10E047.69E07<8.17E071.16E091.26E071.02E099.22E04  
NineMilePointNuclearStationRadiologicalEnvironmentalMonitoringProgramSamplingLocationsTable5.1TypeofSample*MapLocation(Env.CollectionSiteProamNo.)LocationRadioiodineandPaxticulates(air)NineMilePointRoadNorth(R-1)1.8mi888'RadioiodineandParticulates(aix')Co.Rt.29&LakeRoad(R-2)1.1mi8104'SERadioiodineandParticulates(air)Co.Rt.29(R-3)1.5mi8132'ERadioiodineandParticulates(air)VillageofLycoming,NY(R-4)1.8mi8143'E"RadioiodineandParticulates(air)5.MontarioPointRoad(R-5)16.4mi842'EDirectRadiation(TLD)6DirectRadiation(TLD)7DirectRadiation(TLD)8DirectRadiation(TLD)9DirectDirectRadiation(TLD)10Radiation(TLD)llDirectDirectRadiation(TLD)15Radiation(TLD)16DirectRadiation(TLD)12.DirectRadiation(TLD)13.DirectRadiation(TLD)14NorthShorelineArea(75)NorthShorelineArea(76)NoxthShorelineArea(77)NorthShorelineArea(23)JAPEastBoundary(78)Rt.29(79)Rt.29(80)MinerRoad(81)MinerRoad(82)LakeviewRoad(83)LakeviewRoad(84)0.1mi85'0.1mi825'NE0.2mi845'E0.8mi870'NE1.0mi890'1.1mi8115'SE1.4mi8133'E1.6mi8159'SE1.6mi8181'1.2mi8200'SW1.1mi8225'WDirectRadiation(TLD)17DirectRadiation(TLD)18~p-SeeFigures5.1-1and5.1-2SiteMeteorologicalTower(7)0.7mi8250'SWEnergyInformationCenter(18)0.4mi8265' I"IllI'i~IrFJgAQt+!8W+'
~Otktl4!a TABLE.4-16RVALUES-INHALATION
NineMilePointNuclearStationRadiologicalEnvironmentalMonitoringProgramSamplingLocationsTable5.1(Continued)TypeofSample*MapLocation(Env.CollectionSiteProgramNo.)LocationSurfaceWater39DirectRadiation(TLD)19'DirectRadiation(TLD)20DirectRadiation(TLD)21DirectRadiation(TLD)22DirectRadiation(TLD)23DirectRadiation(TLD)24Direct'adiat'ion"(TLD)25DirectRadiation(TLD)26DirectRadiation(TLD)27DirectRadiation(TLD)28DirectRadiation(TLD)29DirectRadiation(TLD)30DirectRadiation(TLD)31DirectRadiation(TLD)32DirectRadiation(TLD)33DirectRadiation(TLD)34DirectRadiation(TLD)35DirectRadiation(TLD)36'irectRadiation(TLD)37SurfaceWater38NorthShoreline(85),NorthShoreline(86)NorthShoreline(87)HickoryGrove(88)LeavittRoad(89)Rt.104(90)Rt.51A(91)MaidenLaneRoad(92)Co.Rt.53(93)Co.Rt.1(94)LakeShoreline(95)Phoenix,NYControl(49)S.W.Oswego,Control(14)Scribe,NY(96)AlcanAluminum,Rt.1A(58)Lycoming,NY(97)NewHaven,NY(56)W.Boundary,BibleCamp(15)LakeRoad(98)OSSInletCanal(NA)JAFNPPInletCanal(NA)0.2mi8294'NW0.1mi8315'W0.1mi8.341'NW4.5mi897'4.1mi8ill'SE4.2mi8135'E4-8mi8156'SE44mi8183'64.4mi8205'SW4.7mi8223'W4.1mi8237'SW19.8mi8170'12.6mi8226'W3.6mi8199'SW3.1mi8220'W1.8mi8143'E5.3mi8123'SE0.9mi8237'SW12mi8101'7.6mi8235'W05mi870'NE(NA)~notapplicable*Map~See'igures5.1-1and5.1-2 Jgv*l11I"~IISI NineMilePointNuclearStationRadiologicalEnvironmentalMonitoringProgramSamplingLocationsTable5.1'Continued)TypeofSample*Map(Env.LocationCollectionSiteProramNo.)LocationShorelineSedimentFishFishFishMilkMilkMilkFoodProductFoodProductFoodProductFoodProductFoodProductFoodProductFoodProduct(CR)404142:43,44454647484950515254SunsetBayShoreline(NA)NMPSiteDischargeArea(NA)NMPSiteDischargeArea(NA)OswegoHarborArea(NA)MilkLocation850MilkLocation87MilkLocation816MilkLocation865ProduceLocation86**(Bergenstock)(NA)ProduceLocation81**(J.Parkhurst)(NA)ProduceLocation82<+(Vitullo)(NA)ProduceLocation85*"(C.S.Parkhurst)(NA)ProduceLocationIII3**(C.Narewski).Produce'Location84**(S.Morris)(NA)ProduceLocation87*"(McMillen)(NA)1.5mi880E0.3mi8315'Wand/or0.6mi855'E6.2mi8235'W9.3mi893'5.5mi8107'SE5.9mi8190'17.0mi8220'W1.9mi8141'E1.8mi896'1.9mi8101'1.5mi8114'SE1.6mi884'2.0mi8-110'SE15.0mi8223'W 1dw,lVCI'E4J'Fc>lI NineMilePointNuclearStationRadiologicalEnvironmentalMonitoringProgramSamplingLocationsTable5.1(Continued)TypeofSample*Map(Env.Location"CollectionSite"'-"ProamNo.)-.LocationFoodProduct'(CR)55:.Produce.Location/$8"*(Denman)(NA)12.6mi8225'WFoodProduct'oodProductFoodProductFoodProduct56575859ProduceLocation/P9"*(O'onnor)(NA)..ProduceLocation810**(C.L~on)(NA)ProduceLocation811**(C.R.Parkhurst)(NA)ProduceLocation812*"(Johnson)(NA)1.6mi6171'2.2mi8123'SE2.0mi8112'SE1.9mi8103ESE6CI*Map-SeeFigures5.1-1and5.1-2**FoodProductSamplesneednotnecessarilybecol1ectedfromalllistedlocations.CollectedsampleswillbeofthehighestcalculatedsiteaverageD/Q.(N/A)~notapplicableCR~ControlResult(location)  
-INFANTI~ram/ruCi/m3NUCLIDEH3Cr51Mn54Pe55Fe59CoSsCo60Zn65Sr89Sr90Zr95I131I133CQ134Cs136Cs137Ba140Ce141T.BODY6.468028.938014.988033.338039.468031.82E031.188043.108041.148042.598062.03804I1.968045.598037.448045.288044.548042.898031.99803GI-TRACT6.468023.568027.058031.098032.478041.118043.188045.138046.398041.318052.178041.068032.158031.338031.438031.338033.83E042.15804BONE1.978041.358041.938043.978054.OSSO71.158053.798041.328043.968054.828045.4SSOS5.59E042.77804LIVER6.468022.538041.178042.368041.228038.018036.258042.788044.438041.92E047.02E051.348056.118055.598011.66804KIDNEY6.46E021.328014.98E033.248043.10E045.178042.248041.908055.638041.728051.348Ol5.24803THYROID6.468025.758011.488073.55806LUNG6.468021.288049.98E058.698041.018067.768054.508066.468052.038061.128071.758067.958041.178047.128041.59806P5.16805  
%W\4"pCC>4r ThBLB.4-17RVhLUES-INHhLhTION
-CHILDmasm/ruCi/m3NUCLIDBH3Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133CQ134CQ136CQ137Ba140Ce141T.BODY1.128031.548029.508037.778031.678043.168032.268047.028041.728046.438063.698042.728047.688032.248051.168051.288054.328032.89803CI-TRhCT1.128031.088032.298042.878037.068043.438049.618041.638041.678053.438056.108042.848035.478033.848034.178033.618031.028055.65804BONE4.748042.078044.258045.998051.018081.908054.808041.668046.50E056.508049.058057.398043.92E04LIVER1.128034.298042.528043.348041.778031.318041.138054.178044.808042.038041.01S061.718058.248056.478Ol1.95804KIDNEY1.128032.43E011.008047.138045.958047.878043.378043.308059.538042.828052.118Ol8.53803THYROID1.128038.538011.628073.84806LUNG1.128031.708041.57S061.118051.278061.10E067.068069.948052.158061.478072.238061.218051.458041.048051748061*5.43805 V4'>>I~<<kA~I<<ff,*Ifl>>'>>-<<ArI<<4>>,~'>>>>N>>I7g>>
TABLE4-18RVALUES-INHALATION
-TEENm~mamimuCi/m3NUCLIDEH3Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133CH134Cs136Cs137Ba140Ce141T.BODY1.27E031.358028.398035.548031.438042.778031.98E046.238041.25E046.678063.158042.648046.218035.488051.378053.118053.518032.16803GI-TRACT1.278033.008036.678046.398031.788059.518042.598054.668043.718057.648051.498056.488031.038049.758031.098048.478032.288051.26805BONE3.348041.598043.858044.348051.08E081.458053.548041.218045.028055.148046.698055.468042.84804LIVER1.27E035.108042.388043.698042.078031.518041.338054.588044.908042.05E041.138061.938058.478056.698011.89804KIOMEY1.278033.078Ol1.278048.63E046.738048.39E043.59E043.75E051.108053.048052.248Ol8.87803THYROID1.278037.498011.468072.92806LUNG1.27E032.098041.988061.24805'.538061.348068.718061.248062.41E061.65E07=-2.688061.468051.778041.218052.038066.13E05 k~I+vs.f1 TABLE4-19RVALUES-INHALATION
-ADULTm~rem/ruC1/m,3eNUCLIDEH3Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136Cs137Ba140Ce141T.BODY1.268039.998Ol6.29E033.948031.058042.078031.488044.658048.718036.09E062.328042.058044.518037.278051.10804GI-TRACT1.268033.32E037.72E046.038031.888051.068052.848055.348043.498057.218051.508056.278038.878031.048041.17E042.568031.53E032.188051.20E054.27E058.39803BONE2.468041.17804.3.248043.048059.91E071.078052.528048.638033.728053.908044.788053.908041.99804LIVER1.268033.958041.708042.778041.588031.158041.03E053.44E043.578041.488048.478051.468056.208054.908Ol1.35804KIDNEY1.268032.288019e838036e898045.418046.12E042.588042e878058.558042.22E051.678Ol6.25E03THYROID1.26E035.948Ol1.198072.15806LUNG1.268031.448041.4087.2181.01806pgc069.758041.208047.518041.278063.618059.278055.968068.638051.408069.59E061.77806 lpga TABLE4-20RVALUES-GROUND-ALLAGEGROUPS2M~modem/e>>Ci/secNUCLIDE1.BODYCr51Mn54Fe55Fe59Co58Co60Zn65Sr89Zr95I.131I133~.Cs134Cs136Cs137"Ba140'Ce141,I135Ba/La140Nb95Sb1254.66E061.34E092.75E083.79E082.15E107.49E082.23E042.49E081.72E072.47E066.82E091.49E081.03E102.05E071.36E07LaterLaterLaterLater PYf4401etr"'g'i,~
NineMilePointNuclearStationRadiological Environmental Monitoring ProgramSamplingLocations Table5.1TypeofSample*MapLocation(Env.Collection SiteProamNo.)LocationRadioiodine andPaxticulates (air)NineMilePointRoadNorth(R-1)1.8mi888'Radioiodine andParticulates (aix')Co.Rt.29&LakeRoad(R-2)1.1mi8104'SERadioiodine andParticulates (air)Co.Rt.29(R-3)1.5mi8132'ERadioiodine andParticulates (air)VillageofLycoming, NY(R-4)1.8mi8143'E"Radioiodine andParticulates (air)5.MontarioPointRoad(R-5)16.4mi842'EDirectRadiation (TLD)6DirectRadiation (TLD)7DirectRadiation (TLD)8DirectRadiation (TLD)9DirectDirectRadiation (TLD)10Radiation (TLD)llDirectDirectRadiation (TLD)15Radiation (TLD)16DirectRadiation (TLD)12.DirectRadiation (TLD)13.DirectRadiation (TLD)14NorthShoreline Area(75)NorthShoreline Area(76)NoxthShoreline Area(77)NorthShoreline Area(23)JAPEastBoundary(78)Rt.29(79)Rt.29(80)MinerRoad(81)MinerRoad(82)LakeviewRoad(83)LakeviewRoad(84)0.1mi85'0.1mi825'NE0.2mi845'E0.8mi870'NE1.0mi890'1.1mi8115'SE1.4mi8133'E1.6mi8159'SE1.6mi8181'1.2mi8200'SW1.1mi8225'WDirectRadiation (TLD)17DirectRadiation (TLD)18~p-SeeFigures5.1-1and5.1-2SiteMeteorological Tower(7)0.7mi8250'SWEnergyInformation Center(18)0.4mi8265' I"IllI'i~IrFJgAQt+!8W+'
NineMilePointNuclearStationRadiological Environmental Monitoring ProgramSamplingLocations Table5.1(Continued)
TypeofSample*MapLocation(Env.Collection SiteProgramNo.)LocationSurfaceWater39DirectRadiation (TLD)19'DirectRadiation (TLD)20DirectRadiation (TLD)21DirectRadiation (TLD)22DirectRadiation (TLD)23DirectRadiation (TLD)24Direct'adiat'ion"(TLD) 25DirectRadiation (TLD)26DirectRadiation (TLD)27DirectRadiation (TLD)28DirectRadiation (TLD)29DirectRadiation (TLD)30DirectRadiation (TLD)31DirectRadiation (TLD)32DirectRadiation (TLD)33DirectRadiation (TLD)34DirectRadiation (TLD)35DirectRadiation (TLD)36'irectRadiation (TLD)37SurfaceWater38NorthShoreline (85),NorthShoreline (86)NorthShoreline (87)HickoryGrove(88)LeavittRoad(89)Rt.104(90)Rt.51A(91)MaidenLaneRoad(92)Co.Rt.53(93)Co.Rt.1(94)LakeShoreline (95)Phoenix,NYControl(49)S.W.Oswego,Control(14)Scribe,NY(96)AlcanAluminum, Rt.1A(58)Lycoming, NY(97)NewHaven,NY(56)W.Boundary, BibleCamp(15)LakeRoad(98)OSSInletCanal(NA)JAFNPPInletCanal(NA)0.2mi8294'NW0.1mi8315'W0.1mi8.341'NW4.5mi897'4.1mi8ill'SE4.2mi8135'E4-8mi8156'SE44mi8183'64.4mi8205'SW4.7mi8223'W4.1mi8237'SW19.8mi8170'12.6mi8226'W3.6mi8199'SW3.1mi8220'W1.8mi8143'E5.3mi8123'SE0.9mi8237'SW12mi8101'7.6mi8235'W05mi870'NE(NA)~notapplicable
*Map~See'igures 5.1-1and5.1-2 Jgv*l11I"~IISI NineMilePointNuclearStationRadiological Environmental Monitoring ProgramSamplingLocations Table5.1'Continued)
TypeofSample*Map(Env.LocationCollection SiteProramNo.)LocationShoreline SedimentFishFishFishMilkMilkMilkFoodProductFoodProductFoodProductFoodProductFoodProductFoodProductFoodProduct(CR)404142:43,44454647484950515254SunsetBayShoreline (NA)NMPSiteDischarge Area(NA)NMPSiteDischarge Area(NA)OswegoHarborArea(NA)MilkLocation850MilkLocation87MilkLocation816MilkLocation865ProduceLocation86**(Bergenstock)
(NA)ProduceLocation81**(J.Parkhurst)
(NA)ProduceLocation82<+(Vitullo)
(NA)ProduceLocation85*"(C.S.Parkhurst)
(NA)ProduceLocationIII3**(C.Narewski)
.Produce'Location 84**(S.Morris)(NA)ProduceLocation87*"(McMillen)(NA)1.5mi880E0.3mi8315'Wand/or0.6mi855'E6.2mi8235'W9.3mi893'5.5mi8107'SE5.9mi8190'17.0mi8220'W1.9mi8141'E1.8mi896'1.9mi8101'1.5mi8114'SE1.6mi884'2.0mi8-110'SE15.0mi8223'W 1dw,lVCI'E4J'Fc>lI NineMilePointNuclearStationRadiological Environmental Monitoring ProgramSamplingLocations Table5.1(Continued)
TypeofSample*Map(Env.Location"Collection Site"'-"ProamNo.)-.LocationFoodProduct'(CR)55:.Produce.Location/$8"*(Denman)(NA)12.6mi8225'WFoodProduct'oodProductFoodProductFoodProduct56575859ProduceLocation/P9"*(O'onnor)
(NA)..ProduceLocation810**(C.L~on)(NA)ProduceLocation811**(C.R.Parkhurst)
(NA)ProduceLocation812*"(Johnson)
(NA)1.6mi6171'2.2mi8123'SE2.0mi8112'SE1.9mi8103ESE6CI*Map-SeeFigures5.1-1and5.1-2**FoodProductSamplesneednotnecessarily becol1ected fromalllistedlocations.
Collected sampleswillbeofthehighestcalculated siteaverageD/Q.(N/A)~notapplicable CR~ControlResult(location)  
*=y"QPr.lY<g~lk 141$I4<o~Ap(IIFIGURE5.(-IHinoMllePointOn.SiteMepgfIOweaewolSWlych'4WJshI>caS%SW~I~NO%/ii111$1$141$I015'I t,"p*,"<~.(4,'e'Et*'>.~<(+tV'II1rlWt"qg'h~q~h*f  
*=y"QPr.lY<g~lk 141$I4<o~Ap(IIFIGURE5.(-IHinoMllePointOn.SiteMepgfIOweaewolSWlych'4WJshI>caS%SW~I~NO%/ii111$1$141$I015'I t,"p*,"<~.(4,'e'Et*'>.~<(+tV'II1rlWt"qg'h~q~h*f  
~t(ltIti~.llillNtI~~tpl0O0CQPl'llEPlOPl  
~t(ltIti~.llillNt I~~tpl0O0CQPl'llEPlOPl  
.r4.JA$tt,sAW+t,O~"C'1+Il APPENDlX-ADOSEPARAMETERSFORlODlNE131AND'l33gPARilCULATESANDTBlTl0liras-88-'-
.r4.JA$tt,sAW+t,O~"C'1+Il APPENDlX-ADOSEPARAMETERS FORlODlNE131AND'l33gPARilCULATESANDTBlTl0liras-88-'-
tt4,HAh0+49&T''IiAw.jL<rW$sa'~'s't~TI4IWl44,1;)hes&2-"ii~r~w"y~~~"y4'~M~'I~vI'Q DOSEPAiUMETERSFORIODINE-131AND-L33iPARTICULATESANDTRITIUMThisappendixcontainsthemethodologywhichwasusedtocalculatethedoseparametersforI-L31,I-L33,particulates,andtritium..Thedoseparameter,Ri,was-calculatedusingthemethodologyoutlinedinNUREG&L33and'Regulatory"GuideL.L09,.Revision'L.-.The-radioiodineandparticulateTechnical.-.;.Specification(Section3.6.15)isapplicabletothelocationintheunrestrictedareawherethecombinationofexistingpathwaysandreceptorage~i..groupsindicates,themaximumpotentialexposureoccurs,i.e.,thecriticalreceptor.Theinhs1ationandgroundplaneexposurepathwaysareconsideredtoexistatalllocationsbutthecriticallocationwillbeusedfordosepurposes.Thegrass-goat-misc,thegrass-cowmQ3c,grass-caveat,andvegetationpathwaysareconsideredtoexistatspecificlocations.Rivalueshavebeencalculatedfortheadult,teen,childandinfantagegroupsforallpathways.ThemethodologyusedtocalculatethesevaluesfoLlows:i,,:.',.,,'i,,A.L,InhalationPathwaR.~K(BR)(DFA)where~+~dosefactorforeachidentifiedradionuclideioftheorganofinterest(units-~mrem/hrperyCi/m);K'BR)(DFA),,'a'constantofunitconversion:-10pCi/qCi;6~Breathingrateofthereceptorofagegroupa,(unitsM/yr);3organinhalation'dose.factorforradionuclideiforthereceptorofagegroupa,(units~mrem/pCi).89-mr~~tW:L~e4q1t+,iA  
tt4,HAh0+49&T''IiAw.jL<rW$sa'~'s't~TI4IWl44,1;)hes&2-"ii~r~w"y~~~"y4'~M~'I~vI'Q DOSEPAiUMETERS FORIODINE-131AND-L33iPARTICULATES ANDTRITIUMThisappendixcontainsthemethodology whichwasusedtocalculate thedoseparameters forI-L31,I-L33,particulates, andtritium..The doseparameter, Ri,was-calculated usingthemethodology outlinedinNUREG&L33 and'Regulatory "GuideL.L09,.Revision'L.-.
~;Thebreathingrates(BR)forthevariousagegroups,asgiveninTableaE-5ofRegulatoryGuide1.109Revision1,aretabulatedbelow.AeGrou(a)BreathinRate(m~/yr)InfantChildTeen-Adult1rr00370080008000lnhalatrondosefactors(DFA.)forthevariousagegroupsaregiveninia"TablesE-7throughE-10ofRegulatoryGuide1.109Revision1.A.2GroundPlanePathwaI(R=K'K"(SF)DFGiXIt(Im)where:GRidosefactorforthegroundplanepathwayforeachIdentifiedradionuclideifOrtheorganofinterest(units=mrem/yrperuCI/secperm)K'.a-constantofunitconversion:10pCI/uCi;6K"=aconstantofunitconversion;8760hr/year; g4Il.l0 theradiologicaldecayconstantforradionuclidei,(units=sec)t=theexposurettme,sec;484.73x10sec(ISyears);DFC.,=thegroundplanedoseconversionfactorforradionuclidei;(units=mrem/hrperpCi/m~)e'F=theshieldingfactor(dlmensionless);IAshieldingfactorof0.7isdiscussedinTableE-15ofRegulatoryCuide1.109Revision1.AtabulationofDFGivaluesispresentedinTableE-6ofRegulatoryGuide1.109Revisionl.A.3Grass-CoworCoat-MilkPathwa-AltfRi-K'QFUF(DFL)eYI+B.(1-e.(I-ff)~ps,tr(tm'YEi+Bi(lmth)ewhere:MRl=dosefactorforthecowmilkorgoatmilkpathway,foreach""'"'identifiedradionuctide''fortheorganofinterest,(unitsmrem/yrperuCi/secperm)..
The-radioiodine andparticulate Technical
0l5~"~4~-I~e'ue't@IE K'aconstantofunitconversion:10pCi/uCi6.QF=Thecow'sorgoat'sfeedconsumptionrate,(units=Kg/day-wetweight)U''hereceptor'smilkconsumptionrate'or-agegroupa,(units=liters/yr);Ytheagriculturalproduct<vitybyunitareaofpasturefeedgrass,(units=kg/m~,);.YItheagriculturalproductivitybyunitareaofstoredfeed,(units=kg/m~);thestableelementtransfercoefficients,(units=pCi/literperpCi/day);r=fractionofdepositedactivityretainedoncow'sfeedgrass:(DFL)=theorganingestiondosefactorforradlonuclideiforthereceptorinagegroupa,(units=mrem/pCi);'heradiologicaldecay-constantfor.radionuclide--i,(units=sec);thedecayconstantforremovalofactivityonleafandplant.surfacesbyweathering~75.73-x10sec.,(correspondingtoa10day.half-life);,.  
.-.;.Specification (Section3.6.15)isapplicable tothelocationintheunrestricted areawherethecombination ofexistingpathwaysandreceptorage~i..groupsindicates, themaximumpotential exposureoccurs,i.e.,thecriticalreceptor.
~rtl~qna tfthetransporttimefromfeedtocoworgoattomilk,toreceptor,(units=sec);th=thetransporttimefromharvest,tocoworgoat,toconsumption,(units=sec);tb=periodoftimethatsoilisexposed.togaseouseffluents,(units=sec);8.concentrationfactorforuptakeofradionuclideifromthesoilbytheediblepartsofcrops,(units=pCi/Kg(wetweight)perpCi/Kg(drysoil);P=effectivesurfacedensityforsoil,(units=Kg(drysoil)/m~);f=fractionoftheyearthatthecoworgoatisonpasture*;f="fractionofthecowfeedthatispasturegrasswhilethecowisonpasture;t=periodofpasturegrassandcropexposureduringthegrowingseason,(units"-sec);<<Milkcattleandgoatsareconsideredtobefedfromtwopotentialsources,pasturegrassandstoredfeeds.FollowingthedevelopmentinRegulatoryCuide1;109Revision1,thevalueoffwasconsideredunityinlieuofs,p'site-specifi.information.Thevalueoffwas.0.667.basedupon,an8-monthgrazingperiod.TableA-1containstheappropriatevaluesandtheirsourceinRegulatoryCuide1.109Revision1.Theconcentrationof>>tritiuminmilkisbasedontheairborneconcentrationratherthanthedeposition.Therefore,theRiisbasedonX/Q:R=KsKts'FQU(DFL)075(05/H)  
Theinhs1ation andgroundplaneexposurepathwaysareconsidered toexistatalllocations butthecriticallocationwillbeusedfordosepurposes.
Thegrass-goat-misc, thegrass-cow mQ3c,grass-caveat, andvegetation pathwaysareconsidered toexistatspecificlocations.
Rivalueshavebeencalculated fortheadult,teen,childandinfantagegroupsforallpathways.
Themethodology usedtocalculate thesevaluesfoLlows:i,,:.',.,,'i,,A.L,Inhalation PathwaR.~K(BR)(DFA)where~+~dosefactorforeachidentified radionuclide ioftheorganofinterest(units-~mrem/hrperyCi/m);K'BR)(DFA),,'a'constant ofunitconversion:
-10pCi/qCi;6~Breathing rateofthereceptorofagegroupa,(unitsM/yr);3organinhalation'dose.factor forradionuclide iforthereceptorofagegroupa,(units~mrem/pCi).
89-mr~~tW:L~e4q1t+,iA  
~;Thebreathing rates(BR)forthevariousagegroups,asgiveninTableaE-5ofRegulatory Guide1.109Revision1,aretabulated below.AeGrou(a)BreathinRate(m~/yr)InfantChildTeen-Adult1rr00370080008000lnhalatron dosefactors(DFA.)forthevariousagegroupsaregiveninia"TablesE-7throughE-10ofRegulatory Guide1.109Revision1.A.2GroundPlanePathwaI(R=K'K"(SF)DFGiXIt(Im)where:GRidosefactorforthegroundplanepathwayforeachIdentified radionuclide ifOrtheorganofinterest(units=mrem/yrperuCI/secperm)K'.a-constant ofunitconversion:
10pCI/uCi;6K"=aconstantofunitconversion;8760hr/year; g4Il.l0 theradiological decayconstantforradionuclide i,(units=sec)t=theexposurettme,sec;484.73x10sec(ISyears);DFC.,=thegroundplanedoseconversion factorforradionuclide i;(units=mrem/hrperpCi/m~)e'F=theshielding factor(dlmensionless);
IAshielding factorof0.7isdiscussed inTableE-15ofRegulatory Cuide1.109Revision1.Atabulation ofDFGivaluesispresented inTableE-6ofRegulatory Guide1.109Revisionl.A.3Grass-Cow orCoat-Milk Pathwa-AltfRi-K'QFUF(DFL)eYI+B.(1-e.(I-ff)~ps,tr(tm'YEi+Bi(lmth)ewhere:MRl=dosefactorforthecowmilkorgoatmilkpathway,foreach""'"'identified radionuctide
''fortheorganofinterest, (unitsmrem/yrperuCi/secperm)..
0l5~"~4~-I~e'ue't@IE K'aconstantofunitconversion:
10pCi/uCi6.QF=Thecow'sorgoat'sfeedconsumption rate,(units=Kg/day-wet weight)U''hereceptor's milkconsumption rate'or-age groupa,(units=liters/yr);
Ytheagricultural product<vity byunitareaofpasturefeedgrass,(units=kg/m~,);.YItheagricultural productivity byunitareaofstoredfeed,(units=kg/m~);thestableelementtransfercoefficients, (units=pCi/liter perpCi/day);
r=fractionofdeposited activityretainedoncow'sfeedgrass:(DFL)=theorganingestion dosefactorforradlonuclide iforthereceptorinagegroupa,(units=mrem/pCi);
'heradiological decay-constant for.radionuclide-
-i,(units=sec);thedecayconstantforremovalofactivityonleafandplant.surfacesbyweathering
~75.73-x10sec.,(corresponding toa10day.half-life);,
.  
~rtl~qna tfthetransport timefromfeedtocoworgoattomilk,toreceptor, (units=sec);th=thetransport timefromharvest,tocoworgoat,toconsumption, (units=sec);tb=periodoftimethatsoilisexposed.to gaseouseffluents, (units=sec);8.concentration factorforuptakeofradionuclide ifromthesoilbytheediblepartsofcrops,(units=pCi/Kg(wetweight)perpCi/Kg(drysoil);P=effective surfacedensityforsoil,(units=Kg(drysoil)/m~);
f=fractionoftheyearthatthecoworgoatisonpasture*;
f="fractionofthecowfeedthatispasturegrasswhilethecowisonpasture;t=periodofpasturegrassandcropexposureduringthegrowingseason,(units"-sec);<<Milkcattleandgoatsareconsidered tobefedfromtwopotential sources,pasturegrassandstoredfeeds.Following thedevelopment inRegulatory Cuide1;109Revision1,thevalueoffwasconsidered unityinlieuofs,p'site-specifi
.information.
Thevalueoffwas.0.667.basedupon,an8-monthgrazingperiod.TableA-1containstheappropriate valuesandtheirsourceinRegulatory Cuide1.109Revision1.Theconcentration of>>tritiuminmilkisbasedontheairborneconcentration ratherthanthedeposition.
Therefore, theRiisbasedonX/Q:R=KsKts'FQU(DFL)075(05/H)  
'l4Awvvml'lsk%k  
'l4Awvvml'lsk%k  
}cher.e:MRTdosefactorforthecoworgoatmilkpathwayfortritiumfortheorganofinterest,(units=mrem/yrperuCi/m');K'"=aconstantofunitconversion;l0~gm/kg;H=absolutehumidityoftheatmosphere,(units"-gm/m~);0.75=thefractionoftotalfeedthatiswater;0-5=theratioofthespecificactivityofthefeedgrasswatertotheatmosphericwater.,.OCOthervaluesaregivenabove.AvalueofHof8grams/meter3,wasusedinlieuofsite-specificinformation.A.OCrass-Cow-MeatPathwa-XitfRiK'~Fap"YXEi+B.(1m(l-ff)r(lmetb+8(leiv)KithesEiR~=ldosefactorforthemeatingestionpathwayforradlonuclideifor.-anyorgan:ofinterest,(units."-mrem/yrperuCi/secperm):-2.F<=thestableelementtransfercoefficients,(units=days/Kg):  
}cher.e:MRTdosefactorforthecoworgoatmilkpathwayfortritiumfortheorganofinterest, (units=mrem/yrperuCi/m');K'"=aconstantofunitconversion; l0~gm/kg;H=absolutehumidityoftheatmosphere, (units"-gm/m~);0.75=thefractionoftotalfeedthatiswater;0-5=theratioofthespecificactivityofthefeedgrasswatertotheatmospheric water.,.OCOthervaluesaregivenabove.AvalueofHof8grams/meter3, wasusedinlieuofsite-specific information.
=S>>I\11lf,~4l~g)AVIPAIIQf4tg}eV~~@Ok>t apthereceptor'smeatconsumptionrateforagegroupa.(units=kg/year;t=thetransporttimefromslaughtertoconsumption,(units=,sec);the,transporttime-.from.,harvest..to,animal"consumpt>on.-(units=sec):t=periodofpasturegrassandcropexposureduringthegrowingseason,(units=sec)""'"'"All'other"<terms-remain'the.sameasdefinedforthemilkpathway.TableA-2containsthevalueswhichwereusedincalculatingR..iTheconcentrationoftritiuminmeatisbasedonairborneconcentrationratherthandeposition.Therefore,theRiisbasedonX/Q.RT=K'K"'FfQU(DFLi)(0.75(0.5/H)Jwhere:dosefactorforthemeatingestionpathwayfortritiumforanyorganofinterest.(units=mrem/yrperuCl/m~).,.Alltermsaredefinedabove.A.SVetationPathwaTheintegratedconcentrationinvegetationconsumedbymanfollowstheexpressiondevelopedfor.milk.Manisconsideredtoconsumetwotypesofvegetation(freshandstored)thatdifferonlyinthetimeperiodbetweenharvestandconsumption,therefore:  
A.OCrass-Cow-Meat Pathwa-XitfRiK'~Fap"YXEi+B.(1m(l-ff)r(lmetb+8(leiv)KithesEiR~=ldosefactorforthemeatingestion pathwayforradlonuclide ifor.-anyorgan:ofinterest, (units."-
mrem/yrperuCi/secperm):-2.F<=thestableelementtransfercoefficients, (units=days/Kg):  
=S>>I\11lf,~4l~g)AVIPAIIQf4tg}eV~~@Ok>t apthereceptor's meatconsumption rateforagegroupa.(units=kg/year;t=thetransport timefromslaughter toconsumption, (units=,sec);the,transport time-.from.,harvest..
to,animal"consumpt>on.
-(units=sec):t=periodofpasturegrassandcropexposureduringthegrowingseason,(units=sec)""'"'"All'other"<terms-remain'the.same asdefinedforthemilkpathway.TableA-2containsthevalueswhichwereusedincalculating R..iTheconcentration oftritiuminmeatisbasedonairborneconcentration ratherthandeposition.
Therefore, theRiisbasedonX/Q.RT=K'K"'FfQU(DFLi)(0.75(0.5/H)
Jwhere:dosefactorforthemeatingestion pathwayfortritiumforanyorganofinterest.
(units=mrem/yrperuCl/m~).,.Alltermsaredefinedabove.A.SVetationPathwaTheintegrated concentration invegetation consumedbymanfollowstheexpression developed for.milk.Manisconsidered toconsumetwotypesofvegetation (freshandstored)thatdifferonlyinthetimeperiodbetweenharvestandconsumption, therefore:  
(Ifih.%'4gAle4.
(Ifih.%'4gAle4.
R.,"-K'(DFL)XitLUfeaLtlm+YIElPX1-X.tbwhere:S'ithUafgetr(l-e)YAhi-AtB(leib),R,=dosefactor.forvegetablepathwayforradionuclldeifortheorganofinterest,(units=mrem/yrperuCi/secperm);K'aconstantofunitconversion;l0pCi/uCi:6LUa=theconsumptionrateoffreshleafyvegetationbytherecepCorinagegroupa,(units=kg/yr);fL=thefractionoftheannualintakeoffreshleafyvegetationgrownlocally;fgthefractionoftheannualintakeofstoredvegetationgrownlocally~..tL...=.,Che.,average.timebetween,harvest--ofleafyvegetationanditsconsumption,.(units=sec);theaveragetimebetweenharvestofstoredvegetationanditsconsumption,(units=sec);Y-thevegetationareadensity,(units=kg/m~);t=periodofleafyvegetableexposureduringgrowingseason(units=sec);  
R.,"-K'(DFL)XitLUfeaLtlm+YIElPX1-X.tbwhere:S'ithUafgetr(l-e)YAhi-AtB(leib),R,=dosefactor.forvegetable pathwayforradionucllde ifortheorganofinterest, (units=mrem/yrperuCi/secperm);K'aconstantofunitconversion; l0pCi/uCi:6LUa=theconsumption rateoffreshleafyvegetation bytherecepCorinagegroupa,(units=kg/yr);fL=thefractionoftheannualintakeoffreshleafyvegetation grownlocally;fgthefractionoftheannualintakeofstoredvegetation grownlocally~..tL...=.,Che.,average
~7I Allotherfactorsaredefinedabove.TableA-3presentstheappropriateparametervaluesandtheirsourceinRegulatoryGuide1.109Revision1.Inlieuofsite-specificdata,valuesforfL.and;fof,1.0'nd'.76,'respectively,wereusedinthecalculation.ThesevalueswereobtainedfromTableE-15ofRegulatoryGuide1.109Revision1.Theconcentrationoftritiuminvegetationisbasedontheairborneconcentrationratherthanthedeposition.Therefore,theR.isbased'onI.X/Q:R=K'K"TUf+UfaLag(DFL)0.75(0.5/H)where:VRTdosefactorforthevegetablepathwayfortritiumforanyorganofinterest,(units=mrem/yrperuCI/m~).Atlothertermsaredefinedinpreceedingsections.
.timebetween,harvest--ofleafyvegetation anditsconsumption,.
JlR~~i'o4~1Ik4[5I TABLEA-1ParametersforCowandGoatMilkPathwaysParameterQF(kg/day)Y(kg/m~)tf(seconds)Value50(cow)6(goat)0.71.73x10(2days)1.0(radioiodines)0.2(particulates)*Reference(R.,Guide1.109Rev.1)TableE-3TableE-3TableE-15TableE-15TableE-15TableE-15(DFL)(mrem/pCi)F(pCl/dayperpCi/liter)t(seconds)Y(kg/m~)Y(kg/m~)t(seconds).U"(liters/yr)t(seconds)EachradionuclideEachstableelement0.73x10(15yr)2.00.77.78x10(90days)330infant330child000teen310adult2.59x106(pasture)65.'18x10(storedfeed)TablesE-11toE-14TableE-1(cow)TableE-2(goat)TableE-15TableE-15TableE-15TableE-15Table'-5TableE-5TableE-5TableE-5TableE-15Bl(pCl/Kg(wetweight)Each-stableelementperpCi/Kg(drysoil))TableE-IP(Kgdrysoil/m~)200TableE-15 IIg+~a~A'.4it@'PCPV TABLEA-2aParametersfortheMeat.PathwayParameterFf(pCi/KgperpCi/day)U(Kg/yr)apValue',1.0(radioiodines)0.2(particulates)Eachstableelement0infant01child.65teen110adultReference(R.Cuide1.109Rev.1)TableE-15TableE-15TableE-1TableE-5TableE-5TableE-5TableE-5,a(DFL)(mrem/pCi)Y(kg/m~)Y(kg/mi)tb(seconds)t(seconds).t(seconds)t.-(seconds)1QF(kg/day)B.,(pCi/Kg(wetweightperpCi/Kg(drysoil))P(Kg(dry=soil)/m~)Eachradionuclide0.72.01.737.782.595.1850x10x10x10x1066x10(15yr)(20days)(90days)(pasture)(storedfeed)200EachstableelementTablesE-11toE-14TableE-15TableE-'lSTableE-15TableE-15TableE-15TableE-15TableE-3TableE-1TableE-15-99-I 4)e"'C/'i TABLEA-3ParametersfortheVegetablePathwayParameterr'(dimensionless)(DFL)(mrem/Ci)U(kg/yr)-infant-child*-teen-adultU(kg/yr)-infantS~-child-teen-adultt<.(seconds)t(seconds)Y(kg/m~)t(seconds)'"t"'(seconds)~P(Kg(drysoil)/m~)81~(pCl/Kg(wetweight)perpCi/kg(drysoll))Value1.0(radioiodines)0.2(particulates)Eachradionuclide026A%2640520630'208.6x10(1day)5.18x10(60days).2.05.18x10(60days).."Oe73x10.(15yr)82aoEachstableelementReference(R.Guide1.109Rev.1)TableE-1TableE-1TablesE-11toE-10TableE-5TableE-5TableE-5TableE-5TableE-5TableE-5TableE-5TableE-5TableE-15TableE-15TableE-15TableE-15TableE-15TableE-15TableE-1;.-.100-IV~"PEP4pih APPENKNX-B";-'NGRAMSOPLNUlDANDGASEOUSRNDNASTETREATMENTSYSTEMS.10.1 PO'I4~rtdpeP4ygCg~,<cyq0+>~>aI+'gifyl\'I(c,4%
(units=sec);theaveragetimebetweenharvestofstoredvegetation anditsconsumption, (units=sec);Y-thevegetation areadensity,(units=kg/m~);t=periodofleafyvegetable exposureduringgrowingseason(units=sec);  
0-CVtaslsIC~4aaph&#xb9;Ss&#xb9;IOK(t&#xb9;hllsllt~lit,t&#xb9;&#xb9;,IID<<penis~elIIIIIOIOILIKt0cene&#xb9;~sweep4(40~IKwnOatahspic~twin~IW'CCKIKKICLKLC~KKIKKsnle~Ia~IP(ItteOPItt~ISlKLIllaeIC~I~I0I~Itt~~I~~IVKOKOsn~0PplplwG.IwsTRuwEwtAwOEoulpwfwTsvvBOLss.((SII(KVI~~ISallIlPl~II~~~I~III~I~!~~s11~~~a(~spt~a(4la~II~I~C(f1ssVa'VIIIa9.OLVA(VtStat(1IL-vol-4(0'K4(saasaae4>>s0(sli~IKPQI'POCP~P''K&#xb9;atKIVCII'I1stKtl'0SnsPKSILIIY~&#xb9;1easSOIWIP(tl(Kstas0L&#xb9;(4(etCKI+>140(PeOseSPVCIIS~IIC/vs~t",&#xb9;nIL'saKIO(pa~rata140thtt01LStle~Catha(0SVIale~isa'4Iln~I&#xb9;I~4'er\LPPI&#xb9;sIIsICO&#xb9;(IIDIPtlllC044allt&#xb9;IIO0~C&#xb9;faCPal(IlesQb)4aleII~IVa(p&#xb9;4+paaoavKsa~aa'D4(4thOC~t'IK>ip<xoovspn~its(~LO4Pa'p0Xnas(DIDPItsl~LoIp'ctpsKLxoaxLclwpPNIYHQ}tggQ.~AV~RA~Tmaaa7aaaaIgrssuueramIttt(I(NO(!JSYALDe&#xb9;Ws40E4sF~~PwLYOODIPCpatD~~PaP~jWSPPCPP(('L'Kl~&#xb9;st~IssoItl~~IKIIPD0(ta00~KIOSK(IttalnIODILDPK(1100~N.,-..-Itsl~CO'e't'IIK&Io4es~I~Ol&#xb9;''C~la~(NOFLOWQteVCat44tkK4QssesCa(44PCICCIal444KID~IK1stasKC-seve4~scspLSateCK&#xb9;alIOIICPNPPSILNOFANS((\tltac&#xb9;taptSIW11llalitIllIW9.KIWIP)P(1ICalYcelacwoLal&#xb9;OCatK.K~CstPJPJI~A(LYIP4~~<ILAIJQILQI~SSoah&#xb9;t14IIII&#xb9;~altDKI+Kalt&#xb9;et(tsVAI,V~POSEDk!JSOA~W$15IHTI-HLI-(L(hco)~>>Steat1aartol&#xb9;stOOPK'+~i4EIL."ALISI0.'IJOINTSSQIIIBQLY6LVE..KSIQIIAEIQH~I~KlPKClaICD~asstKateI~&#xb9;ap&#xb9;s~nlaassDILK~Icaln14ash&#xb9;I-5QIIS}LYLAYUEEIIIIQII.CIIwGIPIPL&#xb9;'4.gtg0~Oil(sees~at&#xb9;PIPIDI}s}(ISK$0~IIIII&#xb9;PIetapacoo>>~Zltl'IsaIIK(ooocL(K8-~~IglteasecICKLI~[VasxsslavettlatKIKO(o7~SaP00(e8--LDL~(O~ILXK1PDKKO~at((O'O'KKIllJsl,&#xb9;sKeOIsaaagogI02-%000,tsttrWO0~~It\DaIKLPKII~~ICLKVlalIt.l4th~naeasallahKPKC40".(?14CleOI-11'IK~KI,FIGUREB0I~SLS&#xb9;I~A'4'~eNIAGARAIOOHAWKPOWERCORPORATIONNINEMILEPOINT-UNIT1OFFSITBDOSSCALCtMANUALVIVII'HSIICLOSCKIAN)C(AIIPKKISIIOOLS egea~v~p1EeI'tr+1f" RADIOACTIVEWASTEDISPOSALSYSTEhrNN%C%(hth(WOI~VIVVCNlhIIVN(tEVIIOVE%$CI,NW~<<I(%VCh0-Cl-0-.JOWICO%COCCI%I(Olh~I%OOOO%V'I'4VWCtIVVO%hNhIWW(hECIIHI-rl.~~INEO%IN~(OWN~NOOO&I%ot~I~!Ovl~hh~~OlVOO3IOIEIN~INONEMh(hl~INVNNVI,OIOgOOWh~INIONCE~COC(vvItvloOWCN%%(tlNIIVI~NNNtOEIVIIhI~ICONNIlvtlIII~I~IOO~ICthlhtNIQIvlloEvvhI~II~N~-M-~-CO(IV'lOWI~NO%IIhtN~IICEIglIIIIIV(wW'hCO%(IN%~W~hNNOI~WIINWOIEI~W%EONCh.~~lttNII(~%(CW%NONOl(tIVVOONI~~NtIIO~IlI~ONEIIVVIVOChOC'V'VIIIh~OIIlh,~~~%(NI(INCOCINNEOWECIIWIIVOItolIO~I~(C$PlLJI"-.';..4iHIIlI.INN~>>NIINIOVIOIOFIGUREIr(oIII3-~NIIoo<<IreIcasrcRlcpocorgyac(EIIIhGARAhIOI4~POINERCaVORAIIONNINEMILEPOINT-UNIT1OFFSITEDOSECALCOhrAIIUAL
~7I Allotherfactorsaredefinedabove.TableA-3presentstheappropriate parameter valuesandtheirsourceinRegulatory Guide1.109Revision1.Inlieuofsite-specific data,valuesforfL.and;fof,1.0'nd'.76,'respectively, wereusedinthecalculation.
~Xs%~~p.l~er<a0ql~I' h7Ti1I>><<I<<IH<<nI~Inn>>ta~g>>Pgl<<<<t>>atat>>InI~Itn<<I~<<an>>I<<~<<>>Inttn<<tat~t<<It<<aIaa'<<I~>><<nttI<<<<Iat~Inn~~<<n~4~~nt.IJ.'PI'I0l>>at<<f~ILi<<nInnCI<<n>>t<<<<at~h>>a<<I>>IIa<<+In<<n~ttt<<IInFIGUAEb-tSac<<acreasedriisuseec4ace~leerSrse~104-~NACA(letLSCSSSAVectSIASSYAS..OACIOSSAllOSJNINEMILEPOINT-UNIT1OFFSIYEDOSECALO.MANUAL  
ThesevalueswereobtainedfromTableE-15ofRegulatory Guide1.109Revision1.Theconcentration oftritiuminvegetation isbasedontheairborneconcentration ratherthanthedeposition.
~~1~A+4Wt'C'4 REACTORBUILDINGVENTILATIONSYSTEMIIVI~eliM~Ihe~Oih0~l(<<t~-QM-mQ.tI~IIga.....~<<KIMO>>OVII<<VVMIOMK<<OIM'VVV~'7~M~IeIMII54'Iag('r.~)'.'.i.MahI~it>L<<(ri~-..5.I/-QM-lg--T~I(IMO>>MVI~ILI(I<<V<<VMMeII~Iv(~4MIV<<t<<~<<IMItVVthtW<<VIIIIVIIVMW~~htiElI~avt0.QNK<<IVI>>M'I<<00MoeofMO(~VaI~Ote~it<<I~~Iht(IIa>>OI~~AMI~(IIMV<<i>>0<<IIVliVi>>V~MeIt~olV("I~e<<vvKJ~IV<<0~IMli~~MIVe>>(VIVIVt<<<<~I<<000.Ot~IMAIi<<0H~IMI<<0I~~~1~<<0~I<<0I~Itl~IMIa~~<<I<<~Melt(VII<<OIMI~Ot~I,<<IOa(I~Ireelvovl'0-~at<<laIvOt(V<<>>I0<<IM~<<aio<<<<IivI<<~ii~ii(M+I<<ll~~~I,>>lIt(~Ej(O>><<II~K(IMI~VI>><<0(V<<VVt(IIV>><<IVKI(Mt<<vtl~IVV~~I~IIV~<<ea(VIlail<<IAiI<<<<<<(<<~~I>>lie<<<<avvv~ev(IM~vv(vIvieiooolii~III~~(0>>00~WVIIV~il~1h<<Mc~Vhlg<<M~<<ItaI~'la~<<M'I>><<'tt"I1IVitt~~1:tttae.tIr-s'~<<V>>ll~OlIt~.0<<tel51~Vti<<0Mt~Iv.5rt:(~400IO.IVOI>>0AIia>>rvl~~<<5.'55k>>v(ett5!i(>>~lI(~~II~<<0IO'ah<<~(55t/'(~'5~I>>V<<~((kt'tI'otPV<<a5<<>>~&0hr'I'ttc>>o'I~~llO>>VJlt.I:JltI~~Al'M(I<<~Illl<<VI~~~IAt~IVVelK<<<<0O>>MV0~Ot<<IflGUAE8EroctorksilJIogYcatllctl((MPyrt(M-IOS-5AGAnal/5uosl/5wxpowERconpollAIlorcNINEMILEPOINT-UNITlOFFSITEDOSECALO.MANUAL 11Tl~~4, WASTEDISPOSALBUILDINGVENTILATIONSYSTChlNlte<<ttII>>ANlett\LA~gM~th~~I.p,~ea>>s\~ICFlNt~<<N3wI-pehhhI~tlhh+N>>H~I'a~NV~VI<<I.r~thNtatV~hlI~I~lethhI~>>V~INciaNh~ahh~I~.>>ICI,eta<<tha>>NCtNtllt~L"':"..-"'I(Mt<<<<IM.[.l..I;;:,.c=::I"i'=....l"NhI>>~te~~I~\~KhteI~h/I'eltat~I~NI~~>>,~IIJiIII~~I'II~~~tel\t<<LII~htWhathe~I~~Ile<<lt~'."I(..jfl~~~WIMhlI.""".'.IJIIIVt~VCSttINI~~h<<et~,I>>~hect~Iv't>>let~1.I)IJ.I)("/-"ef~te!(<<)/./()i,'~~~.'1(i'I'iI,II~~~s'C=':-f=-'I]"L""J;,,-IhCI<<h<<lheLIII~t<<aII.IVl<<>>tati~Ihel<<l,f~ht'IhII<<I~hhaltIa-(")IlII"(-e.I[Qrtiy)l~h>>I~,ejhthhlhIt~I~>>t>>'"'--""("JI~If;1''1I---II~I-teI)iIII~~~~~hh~Itt~~I<<t,fi(aC4~I--JOl~lthIte.)(I)~.,~<<ICh~hh'>>I~ttwtalh~VMh~~lt>>~F.;,l,I.JI;.I-..g..Gth>>ethe>>h<<teI>>.NtV.,;.I<<tCtVatCIVh~Il<<I\tllFIGUAE84RssscIllslhlcslClelg.YsasllsilceaSgslca-I06-tguCSRAIICOIIAWKPOWOICOAIIOIIAIIOIININEMILEPOINT>>UNlT1OFFSITEDOSECALC>>LIAHVAL 4'lj(t4I'IIWI~\hJPIt,~klll STACK-PLANANDELEVATIONF.o'IP4eaJOtLtYATXIIIGRAPNICII~TIOPM~fdR'9.AaTroaI4LLEW'MISOXINKTICPRO11gIPIATroIIM~+~$htLATrOIIMCawCtxvCIOPtCLIO410CLAST@~OfrClSUNESPLAN.0,JI.BT'0'L1LQO'oporTTCL~.SCIIO.:~it~III0ROCX~CL.j'Ir9ELVATIONFIGUREQ>>gLOOKINGNOATH-107-N'-1StickNIAGARAMQHAWKpQWERQQRpQRATIQNNINEMILEPOINTUNIT1OFFSITBDOSECALC~MANUAL ari.7~Aiz'C~4  
Therefore, theR.isbased'onI.X/Q:R=K'K"TUf+UfaLag(DFL)0.75(0.5/H) where:VRTdosefactorforthevegetable pathwayfortritiumforanyorganofinterest, (units=mrem/yrperuCI/m~).Atlothertermsaredefinedinpreceeding sections.
~4Nt44I~~NNl4NkNNI~4AN~I~4N4WtII~NINNINI4~NNIN~~NINtNeIlAll44IINtIN4~I~IIN4NW4I~.ltwt4AI\N~ttINN~N~war4All'444IllNl~IeNtNaNAltNN~tNIII&NtNINII45I'44AtI'4'INIAll44Ill~4Na4Alt~~4NNNI~NINtNAII4FeuAEB-iOlggus~N4INg,VcalIlalltaCFilco-I08-N~~~m~POWERCORPORAIIOHNINEMILEPOINT-UNIT1OFFSITEDOSECALO84ANUAL I,g>gqqP.jAhVlt,t0'4f4  
JlR~~i'o4~1Ik4[5I TABLEA-1Parameters forCowandGoatMilkPathwaysParameter QF(kg/day)Y(kg/m~)tf(seconds)
~~t~)(k)(>)(s)~(b)erewggSASl4SipE)%itC~$i,~t%ICC~NhtCR(c)@(ACACIAfgvfCRCOllOHNtOltAWKATlONK7WC&#xc3;Ll!Tl44gfPFSTATEOFN~VORXMinerRoadLgea~FlGVRE87SiteBoundariesNINEMILE'POINT-109-NIAGARAMO)NWKPODRCORPORAfIONNINEMILEPOINT-UNIT'lOFFSITEDOSECAfCMANUAl.
Value50(cow)6(goat)0.71.73x10(2days)1.0(radioiodines) 0.2(particulates)
*Reference (R.,Guide1.109Rev.1)TableE-3TableE-3TableE-15TableE-15TableE-15TableE-15(DFL)(mrem/pCi)
F(pCl/dayperpCi/liter) t(seconds)
Y(kg/m~)Y(kg/m~)t(seconds).
U"(liters/yr) t(seconds)
Eachradionuclide Eachstableelement0.73x10(15yr)2.00.77.78x10(90days)330infant330child000teen310adult2.59x106(pasture) 65.'18x10(storedfeed)TablesE-11toE-14TableE-1(cow)TableE-2(goat)TableE-15TableE-15TableE-15TableE-15Table'-5TableE-5TableE-5TableE-5TableE-15Bl(pCl/Kg (wetweight)Each-stableelementperpCi/Kg(drysoil))TableE-IP(Kgdrysoil/m~)200TableE-15 IIg+~a~A'.4it@'PCPV TABLEA-2aParameters fortheMeat.PathwayParameter Ff(pCi/KgperpCi/day)U(Kg/yr)apValue',1.0(radioiodines) 0.2(particulates)
Eachstableelement0infant01child.65teen110adultReference (R.Cuide1.109Rev.1)TableE-15TableE-15TableE-1TableE-5TableE-5TableE-5TableE-5,a(DFL)(mrem/pCi)
Y(kg/m~)Y(kg/mi)tb(seconds) t(seconds)
.t(seconds) t.-(seconds) 1QF(kg/day)B.,(pCi/Kg(wetweightperpCi/Kg(drysoil))P(Kg(dry=soil)/m~)
Eachradionuclide 0.72.01.737.782.595.1850x10x10x10x1066x10(15yr)(20days)(90days)(pasture)
(storedfeed)200EachstableelementTablesE-11toE-14TableE-15TableE-'lSTableE-15TableE-15TableE-15TableE-15TableE-3TableE-1TableE-15-99-I 4)e"'C/'i TABLEA-3Parameters fortheVegetable PathwayParameter r'(dimensionless)
(DFL)(mrem/Ci)
U(kg/yr)-infant-child*-teen-adultU(kg/yr)-infantS~-child-teen-adultt<.(seconds) t(seconds)
Y(kg/m~)t(seconds)
'"t"'(seconds)
~P(Kg(drysoil)/m~)81~(pCl/Kg(wetweight)perpCi/kg(drysoll))Value1.0(radioiodines) 0.2(particulates)
Eachradionuclide 026A%2640520630'208.6x10(1day)5.18x10(60days).2.05.18x10(60days).."Oe73x10.(15yr)82aoEachstableelementReference (R.Guide1.109Rev.1)TableE-1TableE-1TablesE-11toE-10TableE-5TableE-5TableE-5TableE-5TableE-5TableE-5TableE-5TableE-5TableE-15TableE-15TableE-15TableE-15TableE-15TableE-15TableE-1;.-.100-IV~"PEP4pih APPENKNX-B";-'NGRAMSOPLNUlDANDGASEOUSRNDNASTETREATMENT SYSTEMS.10.1 PO'I4~rtdpeP4ygCg~,<cyq0+>~>aI+'gifyl\'I(c,4%
0-CVtaslsIC~4aaph&#xb9;Ss&#xb9;IOK(t&#xb9;hllsllt
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~>>NIINIOVIOIOFIGUREIr(oIII3-~NIIoo<<IreIcasrcRlcpocorgyac(EIIIhGARAhIOI4~POINERCaVORAIION NINEMILEPOINT-UNIT 1OFFSITEDOSECALCOhrAIIUAL
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~~1~A+4Wt'C'4 REACTORBUILDINGVENTILATION SYSTEMIIVI~eliM~Ihe~Oih0~l(<<t~-QM-mQ.tI~IIga.....~<<KIMO>>OVII<<VVMIOMK<<OIM'VVV~'7~M~IeIMII54'Iag('r.~)'.'.i.MahI~it>L<<(ri~-..5.I/-QM-lg--T~I(IMO>>MVI~ILI(I<<V<<VMMeII~Iv(~4MIV<<t<<~<<IMItVVthtW<<VIIIIVIIVMW~~htiElI~avt0.QNK<<IVI>>M'I<<00MoeofMO(~VaI~Ote~it<<I~~Iht(IIa>>OI~~AMI~(IIMV<<i>>0<<IIVliVi>>V~MeIt~olV("I~e<<vvKJ~IV<<0~IMli~~MIVe>>(VIVIVt<<<<~I<<000.Ot~IMAIi<<0H~IMI<<0I~~~1~<<0~I<<0I~Itl~IMIa~~<<I<<~Melt(VII<<OIMI~Ot~I,<<IOa(I~Ireelvovl'0-~at<<laIvOt(V<<>>I0<<IM~<<aio<<<<IivI<<~ii~ii(M+I<<ll~~~I,>>lIt(~Ej(O>><<II~K(IMI~VI>><<0(V<<VVt(IIV>><<IVKI(Mt<<vtl~IVV~~I~IIV~<<ea(VIlail<<IAiI<<<<<<(<<~~I>>lie<<<<avvv~ev(IM~vv(vIvieiooolii~III~~(0>>00~WVIIV~il~1h<<Mc~Vhlg<<M~<<ItaI~'la~<<M'I>><<'tt"I1IVitt~~1:tttae.tIr-s'~<<V>>ll~OlIt~.0<<tel51~Vti<<0Mt~Iv.5rt:(~400IO.IVOI>>0AIia>>rvl~~<<5.'55k>>v(ett5!i(>>~lI(~~II~<<0IO'ah<<~(55t/'(~'5~I>>V<<~((kt'tI'otPV<<a5<<>>~&0hr'I'ttc>>o'I~~llO>>VJlt.I:JltI~~Al'M(I<<~Illl<<VI~~~IAt~IVVelK<<<<0O>>MV0~Ot<<IflGUAE8EroctorksilJIogYcatllctl((M Pyrt(M-IOS-5AGAnal/5 uosl/5wxpowERconpollAIlorc NINEMILEPOINT-UNIT lOFFSITEDOSECALO.MANUAL 11Tl~~4, WASTEDISPOSALBUILDINGVENTILATION SYSTChlNlte<<ttII>>ANlett\LA~gM~th~~I.p,~ea>>s\~ICFlNt~<<N3wI-pehhhI~tlhh+N>>H~I'a~NV~VI<<I.r~thNtatV~hlI~I~lethhI~>>V~INciaNh~ahh~I~.>>ICI,eta<<tha>>NCtNtllt~L"':"..-"'I(Mt<<<<IM.[.l..I;;:,.c=::I"i'=....l" NhI>>~te~~I~\~KhteI~h/I'eltat~I~NI~~>>,~IIJiIII~~I'II~~~tel\t<<LII~htWhathe~I~~Ile<<lt~'."I(..jfl~~~WIMhlI.""".'.IJIIIVt~VCSttINI~~h<<et~,I>>~hect~Iv't>>let~1.I)IJ.I)("/-"ef~te!(<<)/./()i,'~~~.'1 (i'I'iI,II~~~s'C=':-f=-'I]"L""J;,,-IhCI<<h<<lheLIII~t<<aII.IVl<<>>tati~Ihel<<l,f~ht'IhII<<I~hhaltIa-(")IlII"(-e.I[Qrtiy)l~h>>I~,ejhthhlhIt~I~>>t>>'"'--""("JI~If;1''1I---II~I-teI)iIII~~~~~hh~Itt~~I<<t,fi(aC4~I--JOl~lthIte.)(I)~.,~<<ICh~hh'>>I~ttwtalh~VMh~~lt>>~F.;,l,I.JI;.I-..g..Gth>>ethe>>h<<teI>>.NtV.,;.I<<tCtVatCIVh~Il<<I\tllFIGUAE84RssscIllslhlcslClelg.YsasllsilceaSgslca-I06-tguCSRAIICOIIAWK POWOICOAIIOIIAIIOII NINEMILEPOINT>>UNlT 1OFFSITEDOSECALC>>LIAHVAL 4'lj(t4I'IIWI~\hJPIt,~klll STACK-PLANANDELEVATION F.o'IP4eaJOtLtYATXIII GRAPNICII~TIOPM~fdR'9.AaTroaI4LLEW'MISOXINKTIC PRO11gIPIATroIIM~+~$htLATrOIIMCawCtxvCIOPt CLIO410CLAST@~OfrClSUNESPLAN.0,JI.BT'0'L1LQO'op orTTCL~.SCIIO.:~it~III0ROCX~CL.j'Ir9ELVATIONFIGUREQ>>gLOOKINGNOATH-107-N'-1StickNIAGARAMQHAWKpQWERQQRpQRATIQN NINEMILEPOINTUNIT1OFFSITBDOSECALC~MANUAL ari.7~Aiz'C~4  
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NOTESTOFIGUREB1(a)NHP1Stack(heightis350')(b)NMP2Stack(heightis430')(c)JAFNPPStack(heightis385')(d)NMPlRadioactiveLiquidDischarge(LakeOntario,bottom)(e)NHP2RadioactiveLiquidDischarge(LakeOntario,bottom)(f)JAFNPPRadioactiveLiquidDischarge(LakeOntario,bottom)(g)SiteBoundary~(h)LakeOntarioShoreline(i)MeteorologicalTower(j)TrainingCenter(k)EnergyInformationCenterAdditionalInformation:-NMP2ReactorBuildingVentislocated187feetabovegroundlevel-.JAFNPPReactorandTurbineBuildingVentsarelocated173feetabovegroundlevel-JAFNPPRadwasteBuildingVentis112feetabovegroundlevel-TheEnergyInformationCenterandadjoiningpicnicareaareUNRESTRICTED.'-4.AREAS"within;,the,SITE~BOUNDARY.thatareaccessibletoHEHBERSOFTHEPUBLIC-LakeRoad,aprivateroad,isanUNRESTRICTEDAREAwithintheSITEBOUNDARYaccessibletoMEMBERSOFTHEPUBLIC5-6 I~II)>>$I'~llh'.AP>>h)">>"h>>Ph~III,>>,IhIIIII PRINTERGRTPARTICULATE00INPUj/DILUTIONSTATIONIODINEDETEGTORS(3)INSTRUMENTATIONCABINETMAINFRAMEFIGUREB8-111-SimplifiedViewofHodel400StackHonitorNIAGARAMOHAWKPOWERCORPORATIONNINEMILEPOINT-UNITtOFFSITEDOSECALC.MANUAL teIIVIf"4~Igr.,ta  
NOTESTOFIGUREB1(a)NHP1Stack(heightis350')(b)NMP2Stack(heightis430')(c)JAFNPPStack(heightis385')(d)NMPlRadioactive LiquidDischarge (LakeOntario,bottom)(e)NHP2Radioactive LiquidDischarge (LakeOntario,bottom)(f)JAFNPPRadioactive LiquidDischarge (LakeOntario,bottom)(g)SiteBoundary~(h)LakeOntarioShoreline (i)Meteorological Tower(j)TrainingCenter(k)EnergyInformation CenterAdditional Information:
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APPENDlX.-CDfSPERStONCALCULATIONTABt.ES  
APPENDlX.-C DfSPERStONCALCULATION TABt.ES  
@~i'O'I~klfgjfg'Ilp'JLfgel4iIC TABLEC-1D/qTABLE(ANHVALMETEOROLOGICALDATA)NNPUNIT+ISIACKCORREC'IKDFOROPENTERRAINRECIRCULATIONtooeeryoooooottooo~toRELATIVEDKPDSTjlDHPERUNlTDIRECTIDHFRONSITE.So''.I.oo1.50e.oo.8>1.040E-0$3.2608-09I.RC<E-I96.78)E-IOSSl)1.806E-OB'3.78TE-09I.<CRE-O'9T.STIE-IOSD7.14IE-09R.4038-099.852E-I~5.413K-IILJSD2.169K-09V.C32E"II3.843K-III.835E-II,wR.<56E-098.59)flo3.CSIE-IOR.OBSE-IODND5.076E-091.74<E-097.<3bK"I~4.ROSE-IONM1.666E-OS<.947E-091.9CIK-IO1.057E-09MNM1.582E-OS1.66RE-O91.814K-IIO.CC9E10H1.5IVE-OS4.701E-091.883K-09I.OR<K-09NHE6.572K-09R.)30E-098.$04E-IO1.96<E-IONE8.968K-09R.CSIE-O9I.IT&K-I95.856K10EWE3.003E-OS8.677E-093.400E-09I.BISE-09E4.315E-OSI.RI3E-IS4.C94E09R.<BIE-09ESE2.837E-OS7.97)K-093.878K-~91.68IE-OOSER.122K-OSC.R5RE-O'9R.43OE-~I).895K-09SSE1.073E-OS3.302E-09I.RTSEI9C.83RE-IOAREAINt~-2)ATFIXEDISTANCESIHNILES2.503.004.2R9K-IO2.$9)E-IO4.9RIE-IO3.367E-IO3.459E-IO2.390E-IOI.IS<E-IO8.260E-II1.3<9E-IO9.<ROE-II8.71)K-IO1.890E-IO6.605E"Io4.51<E-IO6.003E-IO4.086E-IO6.146E-IO4.<RVE-IO3.172E-IO2.198E-IO3.681K-lo8.527E-IOI.IRBE-097.671K-IO1.53'IE-091.037E-099'982K-IO6.755E-IO8.035E-IO5.169E-IO<.R5IEloR.90IE-IO4.004.50I594E-Io1.25IE-IO1.856E-IO).45<E-)01.328E-IO1.042K-IO4.638E-II3.645E-IIS.ROBE-II<.)55E-II1.059E-IO8.3ISE-IIR.<TTE-IO1.936E-IO2.236E-IO1.747K-lo2.145E-IO1.91<E-IO1.22<F.-IO'9.592E-I'I1.389E-IO1.084E-IO1.191E-IO3.87)E-IO5.630Elo4.387E-IO3.667E-IOR.S5TE-IO2.9'92EIo8.338E-IO1.596E-IO1.25)E-IO3.502.I0IE-10R.<<TE-I01.747E-IO6.07<E-II6.927K-II1.389E-IO3.27<E-IO2.957E-IO3.822E-)01.609E-IO1.835E-)05.519E-107.172E-I04.867E-103.957E-I0R.105K"10DPOINTSSYDOLINWINDSECTORS5.00I.OOTE-IOI.ICSE-II8.366K-II8.932E-)l3.339K-lI6.682E-II1.55RE-IOI.<01f-l01.537E-I~7.696E-IIS.CTSE-I'IR.619E-103.51OE-I0R.ROTE-III.875E-III.OOCEIo5.508.878E-II9.5S6E-IIC.SSIE-IIe.<oef-ll2.731K-IIS.469E-)lI.R69E-IO1.1<BE-10I.R59E-II6.29<E-II7.083E-IIR.I<IE-10R.SCSE-IO1.869E-I~1.536E-IO8.861E-III~~0~0~~IOOI~01~~il~lItDIRKCT)OHFROtlSITE8SSHSl)llSDDDHIJNl)NNllNNNENEKNEfESESfSSE6.006.9)TE-IIS.OOIE"II5.704E-II8.000E-II2.27<F.-II1.5<VE-II1.056E-'109.565E-III.0<BE-II5.23)E-II5.879E-III.78IK-IIR.385E-101.555E-III.RBOE-106.903E-II6.505.999E-II6.93<E-II4.963E-III.749f"'II1.988E-II3.973E-II9.127E-II8.256E-II9.092E-I)<.SSSE-II5.083E-II1.535E-IO8.050E-IO1.336E"10I.IOSE"105.979E-II7.005.RISE-IIC.I8IE"II4.379K-III.514E-II1.754E-I)3.505E-I)B.I52E-II7.886E-)IS.IR3E-II4~~IbfII4.<seE-)i1.35<E-I~I.BOSE-I~I.179K-)O9.75IE-II5.e79E-I)7.50<.VISE-IIS.119E-II3.896E"II1.373K-II1.56IE-II3.)ISE-II7.)63E-IIC.<83E"II7.139E-II3.573E-II3.985E-)lI.ROSE-IO1.60BE-IOI.0<BE"108.677K-II<.TOIE-IIDISTANCES8.004.832E-II<.SBCE-II3.<92E-III.23)E-II1.39SE"IIR.794E-II6.<IVE-II5.81OE-II6.39SE-II3.80IE-II3.568E-II1.079K-IOI.<<Of-l09.390E-II7.776K-II4.R)6E-II)Ntl)LES8.503.BRIE-II1.109E-II3.149E-III.IIOE-III.26IK-IIR.5I'9E-IIS.VSSE-II5.240E-)l5.770E-IIR.BS6E-II3.el<E-119.788E-II1.298E-IO8.16<E-II7.01<E-II3.80&E-II9.003.<TOE-II<.OOIE-IIR.BS&E-III.OOTE"11I.I<<E"112.28<E-II5.2<5E-II1.753K-ll5.834E-II2.616E-IIe.912K-II8.8IBE-III.176E-II7.678E"II6.3&RE-)l3.455E-)19.503.167K-ll3.650E"II2.604K-II9.183K-IR1.0<RE-IIR.OSRE-II4.779EII4.333E-II1.77IE-II2.38<E-IIe.&52E-II8.03<E-II1.072E-106.989E-II5.799E-II3.153E-II10.002.904K-ll3.31<E"II2.384E-II8.412E-IR9.5<6E-I21.906E-II4.375E-II3.968E-II4.369E"II8.)822-11R.125E-II7.352E-II9.805E-II6.395E-II5.31)E-II2.890E-IIIS.001.533E-)l1.754K-III.2<RE-II4.393E-IR4.9&SE-IR9.907E-)22.866E-IIR.OCCE-II8.8'16E-II1.130EIII.R45E-)l3.799E11S.054K-II3.30IE-II8.765E-II1.522E-IIeo.oo9.66<E-IR1.099E-II7.742E-IRe.V<6E-le3.097E"le6.168K-leI.105K"II).286K"llI.4IBE-IIT.OIREIR7.663E-IR8.35')E-II3.119E-II8.040E-III.TRRK-II9.569E-IR-114-0'$Iq''tk~'CI~1tgzt'-"JQ',
@~i'O'I~klfgjfg'Ilp'JLfgel4iIC TABLEC-1D/qTABLE(ANHVALMETEOROLOGICAL DATA)NNPUNIT+ISIACKCORREC'IKD FOROPENTERRAINRECIRCULATION tooeeryoooooottooo
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<.)55E-II 1.059E-IO 8.3ISE-II R.<TTE-IO 1.936E-IO 2.236E-IO 1.747K-lo 2.145E-IO 1.91<E-IO 1.22<F.-IO
'9.592E-I
'I1.389E-IO 1.084E-IO 1.191E-IO 3.87)E-IO 5.630Elo4.387E-IO 3.667E-IO R.S5TE-IO 2.9'92EIo8.338E-IO 1.596E-IO 1.25)E-IO 3.502.I0IE-10R.<<TE-I01.747E-IO 6.07<E-II6.927K-II 1.389E-IO 3.27<E-IO 2.957E-IO 3.822E-)0 1.609E-IO 1.835E-)0 5.519E-107.172E-I04.867E-103.957E-I0 R.105K"10DPOINTSSYDOLINWIND SECTORS5.00I.OOTE-IO I.ICSE-II8.366K-II 8.932E-)l 3.339K-lI6.682E-II 1.55RE-IO I.<01f-l01.537E-I~7.696E-II S.CTSE-I'I R.619E-103.51OE-I0R.ROTE-III.875E-III.OOCEIo5.508.878E-II 9.5S6E-II C.SSIE-II e.<oef-ll 2.731K-IIS.469E-)l I.R69E-IO 1.1<BE-10I.R59E-II6.29<E-II7.083E-II R.I<IE-10R.SCSE-IO 1.869E-I~1.536E-IO 8.861E-III~~0~0~~IOOI~01~~il~lItDIRKCT)OHFROtlSITE8SSHSl)llSDDDHIJNl)NNllNNNENEKNEfESESfSSE6.006.9)TE-II S.OOIE"II 5.704E-II 8.000E-II 2.27<F.-II 1.5<VE-II1.056E-'10 9.565E-II I.0<BE-II5.23)E-II 5.879E-II I.78IK-IIR.385E-101.555E-III.RBOE-106.903E-II 6.505.999E-II 6.93<E-II 4.963E-II I.749f"'II1.988E-II 3.973E-II 9.127E-II 8.256E-II 9.092E-I)
<.SSSE-II 5.083E-II 1.535E-IO 8.050E-IO 1.336E"10 I.IOSE"105.979E-II 7.005.RISE-II C.I8IE"II4.379K-II I.514E-II1.754E-I) 3.505E-I)
B.I52E-II7.886E-)I S.IR3E-II4~~IbfII4.<seE-)i 1.35<E-I~I.BOSE-I~I.179K-)O9.75IE-II5.e79E-I) 7.50<.VISE-IIS.119E-II3.896E"II 1.373K-II 1.56IE-II3.)ISE-II 7.)63E-IIC.<83E"II7.139E-II3.573E-II 3.985E-)l I.ROSE-IO 1.60BE-IO I.0<BE"10 8.677K-II
<.TOIE-IIDISTANCES 8.004.832E-II
<.SBCE-II 3.<92E-II I.23)E-II1.39SE"IIR.794E-II 6.<IVE-II5.81OE-II6.39SE-II 3.80IE-II3.568E-II 1.079K-IO I.<<Of-l09.390E-II 7.776K-II 4.R)6E-II)Ntl)LES8.503.BRIE-II 1.109E-II3.149E-III.IIOE-III.26IK-IIR.5I'9E-IIS.VSSE-II 5.240E-)l 5.770E-II R.BS6E-II 3.el<E-119.788E-II 1.298E-IO 8.16<E-II7.01<E-II 3.80&E-II 9.003.<TOE-II<.OOIE-II R.BS&E-II I.OOTE"11 I.I<<E"112.28<E-II5.2<5E-II 1.753K-ll 5.834E-II 2.616E-IIe.912K-II8.8IBE-III.176E-II7.678E"II 6.3&RE-)l 3.455E-)1 9.503.167K-ll 3.650E"II 2.604K-II9.183K-IR 1.0<RE-IIR.OSRE-II 4.779EII4.333E-II 1.77IE-II2.38<E-II e.&52E-II 8.03<E-II1.072E-106.989E-II 5.799E-II 3.153E-II10.002.904K-ll 3.31<E"II2.384E-II 8.412E-IR 9.5<6E-I2 1.906E-II 4.375E-II 3.968E-II 4.369E"II 8.)822-11 R.125E-II7.352E-II 9.805E-II 6.395E-II 5.31)E-II 2.890E-II IS.001.533E-)l 1.754K-II I.2<RE-II4.393E-IR 4.9&SE-IR 9.907E-)2 2.866E-II R.OCCE-II 8.8'16E-II 1.130EIII.R45E-)l 3.799E11S.054K-II3.30IE-II8.765E-II 1.522E-II eo.oo9.66<E-IR1.099E-II 7.742E-IR e.V<6E-le 3.097E"le 6.168K-le I.105K"II).286K"ll I.4IBE-IIT.OIREIR7.663E-IR 8.35')E-II 3.119E-II8.040E-II I.TRRK-II 9.569E-IR
-114-0'$Iq''tk~'CI~1tgzt'-"JQ',
TABLEC-2D/gTABLE(GRAZINGSEASONMETEOROLOGICAL DATA)HHPUNIT<4ISTACKCORRECTED FOROPEHTERRAINRECIRCULRELAT)VE~tttt1~10~00~I~10ttrO~AT)ONDEPO817)ON PERUN)TAREA)Nil-RfATFIXEDPOINTSBYDOUIIUIHD SECTORS0~~00~~11I~t~~1~OtttOD)RECT)ON FRON81'TE8SSllSUUSUUNUNilHkliNNNENEEHKEESESESSE.50'1.001.079E-OS 3.3e<E-09
).030K-OS 3.R<RE-O'9 5.999E-09 1.97<K-ot 1.658E-09 5;t39K-10 I.sVRE-09 6.736E-IO
<.629E-09 1.579E-~9).586E-OS
<.VBRE-~'91.556E-OB
<.658E-09 1.63)K-OS 5.076E-09 6.522E-09 2.113E-49 7.276E-09 R.Reef-ot 2.9SSE-OS 8.799K-O'9 3.971E-OB I.1<3E-082.30SE-OS C.595E-09 1.880E-OB 5.557E-49 1.120E-OB 3.3&IE"09 1.54I.RTOE-09 I.RTOE-~9S.47<E-I4R.SRCE-I~R.918E-I~C.CTTE-I~1.90&E"09 I.8ISE-09R.03)f-ot S.BORE-I~9.I<IK-143.<89E-09
<<.CIE-at8,553E-atR.l<3E-09 I.RTTE-49 2.006.7<BE-IO C.B<9E10<<.C<E-IOI.<3RE-I~I.C6RE-I03.7&OE-I4
).032E-09 9.78SE-IO I.105E-09<.899E-14 5.028E-14 I.BBOK-09 8.375K-ot 1.3538-09 I.138E-09C.7<3E-I~DISTANCES 1NI)ILESR.503.003.50<.)82K-IOR.8<BE-IO 2.06<E-IO
<.RSTE-Io 2.93&E-IO R.)36E-)O 2.839E-IO 1.96<E-)0 I.<36E-IO 9.253E-)l 6.<63E-II
<.757E-II I.OVSE-'Io 7.5<BE-I'I 5.5&OE-II 2.<ISE-IO 1.683K-IO 1.236K-IO 6.<68E10<<.30E"lo3.217K-IO 6.055E-IO
<.129E-Io 2.993E"10 C.953E-IO
<.776E-10 3.<TVE-IO 3.IRTE-!0 R.l&VE-IO 1.585E-IO 3.18SE-IO 2.)9<E-IO 1.598E-)0 I.176E-098.036E-)0 5.829E-IO I.<73E-09 I.OOIE-09 7.236EIo$.361K-IO5.672E-IO
<.09<K-IO 7.0<5E-IO
<.789E-IO 3.<6<E-IO
<.16)E-Io 2.82<K-IO 2.0<RE-IO
<.001.565E-IO
).622E-IO 1.093K-I~3.63SE-II
<.2<9E-II 9.<23E-II 2.<37E-10R.265E-IO e.&39E-lo l.eo&f-lo I.RlefI0<<.IRE-)45.<63EIo3.089EIoR.&Itf-101.5<SE-)0
<.50I.RRTE-IO I.eVef-lo 8.580E-II 2.859E-II 3.3<OE-II 7.39SE-II 1.906E-IO I.77ef-Io2.067E-IO 9.<5)K"II9.<TBE-II 3.<<SE-IO<.263E-IO e.<Iof-Io2.0<BE-IO I.RIOE-IO 5.009.876E-II 1.023E-IO 6.898E-II 8.300E-)l R.&86K-II 5.9<5E-II 1.5RSE-IO 1.<eeE-IO 1.659E-14 7.585EII7.59IE-II2.76<E"lo 3.<I<EIOI.930E-10I.6<<E-10t.TRSE-II 5.50S.)ROE-II 8.<OIE-II 5.65SE-II 1.88&E-II R.ROOE-II
<.867E-II I.RSIE-I0 I.I&5E-101.360E-IO 6.205E-II 6.1')9E-Il 2.26)K-I08.798E-IO 1.579K-)4 1.3<TE-IO 7.'993E-II DIRECT)OH FROHSITK8SSllSIII)SUUUHUNUNHll.HHkfNEENEEESKSESSE6.006.796E-)l 7.0)SE-II
<.7)RE-III.57IE-II1.830E-II
<.0<9E-II I.0<IE"I09.71<E-II1.133K105.158E-II 5.I<6E-II1.882E"10 8.323E-)0 1.31<E-I0I.IR<E-106.68<K-II 6.505.88<EII6.090E-II
<.IOSE-II1.375E-II 1.603E"II 3.536E-II 9.007E-II 8.397K-II 9.828K-II
<<.9)K-11<<.CRE-II1.627E-IO R.OOIE-IO I.13)E-I~9.702E-II 5.77<K-II 7.0~5.197E-II 5.377K-II 3.CR3E-III.RI<E-'III.<I<EII3.)ROE-II 7.9<TE-II 7.<IIE-II 8.673E-II 3.tCRE-II 3.935E-II I.@35E-I4 I.TCSE-I~'t.tSRK-II 8.56<E-II S.ottf-ll 7.50<.Ceif-Ii
<.78TE-II3.22<K)11.080E-II 1.858E-II 8.77&E-II 7.069E-II C.595E-II 7.717E-II 3.52<E-II 3.<99E-II I.eTTE-io I.STOE-148.879K-II 7.622E-II
<.5<OE-II D)STANCES 8.00<.153EIf<.29<E-II 8.890E-I) 9.682K-le I.IRTE"II'.<BVE-)l 6.33<E"II 5.91)E-II C.t)TK-II 3.157K"II 3.133E-III.I<<E-I01.<OTE-107.95SE-I)
C.833E-II
<.473E-ll IHH)LES8.503.750E-II 3.876E-II 8.60TE-)l S.73<K-IR I.0ITK-II2.2<3E-II 5.71)E-fl 5.332K-ll 6.239E-I)
R.B<6E-)l 2.823K-ll 1.03IE-10 I.R&SE-IO 7.ITRE-II6.I&5E-II3.677K-ll 9.003.<06f-ll 3.518E-II8.366E-II T.tesf-ie 9.220E-IR 2.03<K-II 5.)TSE-II
<.837E-II 5.659E"II 2.580K-II e.ssBE-)l 9.350E-II I.150K-I06.542E-II 5.593K-ll 3.338K-ll 9.503.149E-1I3.210E-II 2.157EII7.2RTE-)8 8.<05E-IR 1.85<E-II
<.7)9K-II
<<.IIE"II5.164K-ll 2.35)E-II R.370E-II B.seof-ll 1.0<VE-IO 5.985K-II 5.)0IE-II3.0<7K-II 10.002.85)E-)l 8.9<3E-II 1.976E-)f 6.62)E-IR7.698E-)8I.698E-II<.320E-ll
<.0<OE-II
<.726E-If R.152E"ll8.13)E-II 7.799E-II 9.58TE-II 5.<2<E-II
<.673E-)1 R.793E"II
)5.001.508E-II 1.5<9E-)l 1.03<K-II 3.<65E-IR
<.~IRK-)28.838E-I2R.2<IE-11R.IOSE-fIR.<65f-ll I.I)6E-I)1.097E-II
<.0<2E-II
<.957E-ll 2.808K-ll e.<<ef-lII.<73E-II20.009.52)f-I29.7<IE-126.<67E-122.)TOEIRR.so<f-le 5.509K-IR 1.392K-I) 1.3)5E-II1.538E-II6.930E-IR 6.766E-IR 2.508E-II 3.069K-lf 1.7<OE-II 1.585E-II t.ecSE-IR
-115-F~IFf<<'t<<'FIItC<<<<I TABLEC-3x/q(hHNUALHETEOROLOGICM.
DATA)NNPUIIITO'ISTACKNDDECAY,UNDEPLETEQ CDRREC1EO fQRQPEII1fRRhlNRECIRCULATION 4hlttIUALAVERACKCtlt/0IBKC/NETER CUSEOl.500I.oooI.50'.I07E07'9.910K-DS 4.R64K-OS 4.880K-OT I.209E-OT 5.I33E-OS 3.851K-or 9.486K-os 4.o46f-os R.o<<f-or4.984K-os e.092E-os 2.802K-or 6.13IE-DS R.TSTK-OS 4.206E"Dl I.028E-OY 4.3RCE-DS I.IItf-062.695K-OY 1.DBTE-OTl.062E-DC R.555K-OT I.ORYE"01 I.II3E-062.705K-OT I.IOIE-076.664E-DT I.6llf-or 6.5COE-OS 7.774E-DY I.855E-OY 7.430K-OB I.390E-DC 3.316E-~7l.3CTK-DT l.550E-06 3.789K-O7 I.54lf-~78.385E-OT 2.044K-OT 8.386K-OS 5:921E-or I.459K-or 6.lace-oa3.641E-07 S.'l98f-08 3.7CRK-OS BEC10R8SSMBMMSMMMNMNMIttIMIIttttENEEtlfEESESf5SEe.ooo2.558E-OS 3.052K-OS R.463E-OS I.R73E-OS I.678E-OS 2.6lrf-os C.292E-OS 5.89SE-OB C.422E-OB 3.859E-OS 4.275E-OS 7.817E-088.87DE-DS 4.86RE083.Cl9f-08e.eoof-oa I.BDRE-OB 2.I32E-08I.766E-OS 9.289K-ot l.e<<f-ool.s'YDK-DB 4.340K-OS 4.04IE-OB 4.459K-DB R.7IIE-OS 2.939K-OB 5.38IE-OB 6.036K-OB 3.323K-OS R.559K-DB I.593E-OS l.386E-DB I.626K-DB l.317E-DB 7.436E-09 9.590K-09 1.45fE-OS 3.292E-DB 3.052K-OB 3.403E"08 2.092E-DB R.RRBE-OB 4.036E-OS 4.501E"082.486K-os I.936K-OB I.225E-OS DISTANCEINNILESe.5oo3.ooo3.500I.I24E-OB I.309E-OB I.IRBE-OS 6.265K-09 B.DOBE-09 I.I92E-OB2.643K-OO 2.445E-OB 2.747E-DB l.706K-OB I.Y92E-OB 3.ROSE"08 3.564E-OS
'I.961K-OSI.544E-OB 9.926E-09 4.000'9.449K09I'92E-089.545E-09 5444E-096.908E-09 I~OOBK-OS2.203E-OS 2.03'IE-08 e.3olE-oa I.44IE-OS I.498E-OB R.644E-DB 2.930E"08 I.CITE-OS I.R75E-088.333K-ot 4.5005.'000S.I44E-09T.ISBE-D'9 9.34BE-O9 S.I66E-09 8.260K-ot 7.276K-ot 4.829E-D9 4.349K"09 6.09IE-09 5.451E-09 B.1I9E"09 1.611E-09 I.885E-DB l.644K-OB I.743K-OB I.SRRE"08 I.97TE-08I.732E-08I.247E-OS I.099E-OB I.RBYE-oa I.leaf-os R.e42f-oa I.942K-os R.477E-OB R.140K-OS I.366K"08 I.I79E-DS I.OSIE-OS
'9.365f-ot Y.I73E-09 6.300E-09 5.500C.3885-09 7.244E-09 6.4tYf-093.96IE-094.94SE-09 6.85IE-09 I.457K-08I.35IE-08I.540E-OB 9.8ICE-09 l.004E-OS I.1IOE-08I.SSOE-OS I.035K"08 8.24IE-095.6ITE"09hlttlUALAVERACKSEARINCBSMCMUOMItMtlMIIMtMIMtltttlfNEEttfEEBESE.SOECttl/0IBEC/METER CUBKQl6.0006.5007~Oo~5.765K-09 5.27TK-O'9 4.89'TE-Ot 6.503E-09 5.'923E-09 5.413K-ot 5.863E-09 5.363K-09 4.975K-ot 3.640E-09 3.384E-ot 3.I84K-09 4.5R9E-09 4.l'trf-09 3.939K-09 6.IBIE-09 5.653E-~95.242K-O'9 I.306E-DB I.189E-OS I.DOTE-OS I.RI3K-OS I.I05E-OBI.ORRE-DS l.386E-DS I.265K-.OS I.ITIK-088.86tf-09 S.IRRE-09 7.542K-09 9.039E-09 S.R63E-09 T.CC4K-09 I.525K-OB l.38IE-DB I.RTDKOS1.673E-OS I.5IRE-OS l.38SK-OS 9l99f-098.308E-Ot T.CISE-~97.3442-09 6.644K-ot C.'IDRKOt5.065E-09 4.633E"09 4.Rtlf-ot 7.5004.568E-D9 5.080E-09 4.633K-09 3.005K-O'9 3.708K-D9 4.88IE-09 I.OIBE-DS 9.496E-O'9 I.089K-DS 1.0'33E-0'9 7.I4IE-09l.l74E-OB l.28IE-OS 7.023E-09 S.C33f-o'9 4.004E-09 4.275K-09 4.735K-09 4.330E"09 2.842K-ot 3.500K-O'9 4.562E-D9 9.417K-09 8.859E-09 I.OITE-OB 6.'582K-09 6.68IK-09 l.090K-OS l.lsrf-oa 6.505E-09 5.223K-09 3.744E-09 4.0I4E-09 4.429E-09 4.060E-09 2.695K"09 3.3I2K-09 4.277E-09 8.858E-09 S.R94f-ot 9.526E-09 6.I79E-096.273E-09 I.DICE-08I.ID5E-086.050E-09 4.863K-09 3.5I3E-09 Q!STANCEItltllLESS.DDD8.5009.00D3.780E-09 4.I55E"09 3.BISE-09 2.560K-09 3.I4IE-09 4.022E-09 8.307K-09 7.7'tOE-09 8.953E-09 5.BISE-09 5.908K-09 9.5075-0'I I.O'33E"08 5.648E-09 4.544E-09 3.306E-09 9.5003.570E093.9IOE"09 3CDOE-092.436E"09 2.985E-09
'3.792K-09 Y.BI3E"09 7.338E0'98.437EDt5.493E-09 5.580E-09 8.924E-09 9.CYBE-095.R90E"09 4.P59K093.II9E-09I0.000I5.0003.380E-09 2.269K-O'9 3.C90E-09 R.414E-09 3.403K-09 2.254K092.323E-09 I.C35E092.842E-09 I.983E093.585E-09 2.375E-09 7.368E-D'9 4.SORE096.93IK"09 4.573E-09 7.972E-09 5.210E-09 S.I98E-09 3.474E"09 5.2$4f-ot3.5&6E-09 8.40RE-09 5.4Rtf-09 9.099E-09 5.SIDE"09 4.970E"09 3.I59E-09 4.004E-09 R.S60E-09 R.95IE-09 I.OCOK09eo.oool.689E-09 l.764K-09 1.659K-09 l.e47E-09 I.506E-09 1.748E-09 3.498E-09 3.362E-09 3.876E-09 2.570E-09 2.666E-09 3.950E-09 4.I91E-09R.ersf-ot I.852K-09 I4h7F44
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/'IlaIFd}}
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Revision as of 03:42, 29 June 2018

Forwards Semiannual Radioactive Effluent Release Rept Jan- June 1990 & Revs 6-8 to Odcm. Radioactive Effluent Release Rept Includes Summary of Liquid,Gaseous & Solid Effluents & Justification for Revs to ODCM
ML18038A323
Person / Time
Site: Nine Mile Point Constellation icon.png
Issue date: 08/30/1990
From: FIRLIT J F
NIAGARA MOHAWK POWER CORP.
To:
NRC OFFICE OF INFORMATION RESOURCES MANAGEMENT (IRM)
Shared Package
ML17056A964 List:
References
NMP67505, NUDOCS 9009110036
Download: ML18038A323 (513)
v • d • e


Text

ACCELERATED DISTSJBUTION DEMONSTFWTION SYSTEMREGULATOR INFORMATION DZSTRIBUTZONeSTEM (RIDE)/~,ACCESSION NBR:9009110036 DOC.DATE:

90/08/30NOTARIZED:

NODOCKETFACIL:50-220 NineMilePointNuclearStation,Unit1,NiagaraPowe0500220AUTH.NAMEAUTHORAFFILIATION FIRLITFJ.F.

NiagaraMohawkPowerCorp.RECIP.NAME RECIPIENT AFFILIATION DocumentControlBranch(Document ControlDesk)

SUBJECT:

Forwards"Semiannual Radioactive EffluentReleaseReptforJan-June1990"&Rev6-8ofODCM.IDISTRIBUTION CODE:ZE48DCOPIESRECEIVED:LTR

)ENCLgSIZE:4'fTITLE:50.36a(a)(2)

Semiannual EffluentReleaseReportsNOTES:RECIPIENT IDCODE/NAME PD1-1LAMARTIN,R.

INTERNAL:

ACRSTECHADVRE~01RGN1DRSS/RPBEXTERNAL:

BNLTICHLER,J03 NRCPDRCOPIESLTTRENCL1111221111RECIPIENT IDCODE/NAME PD1-1PDAEOD/DSP/TPAB NRR/DREP/PRPB11 RESBROOKS,BRGN1FILE02EG&GSIMPSON,F COPIESLTTRENCL111122111122DDDNOTETOALL"RIDS"RECIPIENTS:

PLEASEHELPUSTOREDUCEWAS'ONTACT THEDOCUMENTCONTROLDESK,ROOMPl-37(EXT.20079)TOELIMINATE YOURNAMEFROMDISTRIBUTION LINISFORDOCUMENTS YOUDON'TNEED!DDTOTALNUMBEROFCOPIESREQUIRED:

LTTR19ENCL

'v"gg~swr~0LIrf*(4) i4NINEMILEPOINTNUCLEARSTATION/P.O.

BOX32,LYCOMING, N.Y.13093/TELEPHONE (315)343-2110August30,1990U.S.NuclearRegulatory Commission Attn:DocumentControlDeskWashington, DC20555RE:NineMilePointUnitg1DocketNo.50-220DPR-63Gentlemen:

Inconformance withtheNineMilePointNuclearStationUnitglTechni~cal Specifications, weareenclosing theSemi-Annual Radioactive EffluentReleaseReortfortheperiodJanuary1,1990,throughJune30,1990.Includedinthisreportisasummaryofliquid,gaseousandsolideffluents releasedfromthestationduringthereporting period(Tables1-3),adescription ofandjustification forrecentrevisions totheOffsiteDoseCalculation Manual(ODCM)(Table4),anexplanation astothecauseandcorrective actionsregarding theinoperability ofanyStationLiquidand/orGaseousEffluentMonitoring instrumentation (Table5,andAttachment 1),adescription ofrecentrevisions totheProcessControlProgram(PCP)(Table6),andanupdateofactualdataforthemonthofDecemberusedinthefourthquarteroftheJuly-December1989Semi-Annual Radioactive EffluentReleaseReport(Table7).Copiesofrevision6,7and8oftheUnit1ODCMandrequiredtechnical reviewdocumentation arealsoenclosed.

ITheformatusedfortheeffluentdataisoutlinedinAppendixBofRegulatory Guide1.21,Revision1.Doseassessments weremadein,accordance withtheNMP-1Off-SiteDoseCalculation Manual.Distribution isinaccordance withRegulatory Guide'0.1, 10CFR50.4 (b)(1)andtheTechnical Specifications.

Ifyouhaveanyquestions concerning theattachedreport,pleasecontactGaryCorell,Chemistry UnitSupervisor, atNineMilePointUnit1(315)349-2070.

Verytrulyyours,900911003b 900830PDRADQCN,05000220RPNUJFF/lmcEnclosures (3copies)osephFFirlitVicePresident

-NuclearGeneration I~r t,Page2U.S.NuclearRegulatory Commission August30,1990xc:Director, OfficeofNuclearReactorRegulation (1)Director, OfficeofInspection andEnforcement (1)Mr.ThomasT.Martin,RegionalAdministrator, UnitedStatesNuclearRegulatory Commission, RegionI,Allendale Rd.,KingofPrussia,Pennsylvania 19406(1)NRCResidentInspector, NineMilePointNuclearStationUnit51(1)NewYorkStateEnergyOffice,2Rockefeller Plaza,Albany,NY12223Attn:Ms.DonnaRoss OFF-SITEDOSECALCULATION MANUALNINEMILEPOINTUNIT.1

~vr"<<.J'qw(,W~Pg ODCH-NINEMILEPOINTUNIT1TABLEOFCONTENTS

1.0INTRODUCTION

2.0 LIQUIDEFFLUENTS

2.1SetpointDeterminations 2.1.1Basis2.1.2ServiceWaterSystemEffluentAlarmSetpoint2.1.3LiquidRadwasteEffluentAlarmSetpoint2.1.4Discussion 2.1.4.1ControlofLiquidEffluentBatchDischarges

'::2:1-'."4:2'>.Simultaneous:

Discharges.of'Radioactive Liquids2.1.4.3SampleRepresentativeness 2.1.4.4LiquidRadwasteSystemOperation 2.1.4.5ServiceWaterSystemContamination

'.2-'iquidEffluentConcentration Calculation

~Pae~-102.32.3.13.03.13.1.13.1.23.1.3DoseDeterminations MaximumDoseEquivalent PathwayGASEOUSEFFLUENTS

'Setpoint Determinations BasisStackMonitorSetpoints Recombiner.

Discharge (OffGas)MonitorSetpoints 121217171718213.1.4Emergency Condenser VentMonitorSetpoint223.1.53.1.5.13.1.5.2Discussion StackEffluentMonitoring SystemDescription Stack.SampleFlowPath-RAGEHS2323.3.1.5.3.StackSampleFlowPath-OGESHS25 Ae,f/f,iI4)"4'pa'tkW ODCM-NINEMILEPOINTUNIT1TABLEOFCONTENTS(Cont'd)3.1.5.4-SampleFrequency/Sample Analysis=

3.1.5.5I-133Estimates 3,1.5.6GaseousRadwasteTreatment SystemOperation

~Pae2627273.23.2.1DoseandDoseRateDetermination DoseRate28313.2.1.1NobleGases3.2.1.2Tritium,IodinesandParticulates 31333.2.2Dose353.2.2.1NobleGasAirDose3.2.2.2TritiumIodinesandParticulates 3.2.2.3Accumulating Doses3637383.3CriticalReceptors 39e4.O4.140CFR190REQUIREMENTS Evaluation ofDosesFromLiquidEffluents 3.4Refinement ofOffsiteDosesResulting FromEmergency Condenser VentReleases41424.2'.34.45.05.15.25.3Evaluation ofDosesFromGaseousEffluents iEvaluation" ofDosesFromDirectRadiation DosestoMembersofthePublicNithintheSiteBoundaryENVIRONMENTAL MONITORING PROGRAMSamplingStationsInterlaboratory Comparison ProgramCapabilities forThermoluminescent Dosimeters UsedforEnvironmental Measurements.

484849535556

<<YIU,L'b4QtgI ODCH-NINEMILEPOINTUNIT1TABLEOFCONTENTS(Cont'd)~PaeTablel-lAverageEnergyPerDisintegration Tables2-1AiatValuesfortheNMP-1Facilityto2-8Table3-1CriticalReceptor-Dispersion Parameters forGround.LevelandElevatedReleasesTable3-2GammaAirandHholeBodyPlumeShineDoseFactorsforNobleGases(BiandVi)Table3-3Immersion DoseFactorsforNobleGasesTables3-4'to3-22">>OrganDoseandDoseRateFactors(Ri)Table5-1NMP-1Radiological Environmental Monitoring ProgramSamplingLocations Figure5.1-1NineMile'oint On-S/teHapFigure5.1-2.NineMilePointOffsiteHap5960.68697071909495AppendixALiquidDoseFactorDerivation (Aiat)AppendixBPlumeShineDoseFactorDerivation (BiandVi)...Appendix C.OrganDoseandDoseRateFactorsforIodine-131and133,Particulates andTritiumDerivation (Ri)AppendixDDiagramsofLiquidandGaseousRadwasteTreatment Systems97100104115 l>dI1a

1.0INTRODUCTION

'heOffsiteDoseCalculation Manual(ODCM)providesthemethodology tobeusedfordemonstrating compliance withtheRadiological EffluentTechnical Specifications (RETS),10CFR20,10CFR50,and40CFR190.ThecontentsoftheODCMarebased-on.,Draft NUREG-0472, Revision3,"Standard Radiological

'Effluent Technical;Specifications forPressurized Hater...Reactors,"'September 1982;DraftNUREG-0473, Revision2."Radiological EffluentTechnical Specifications forBNR's","July1979;NUREG0133,"Preparation ofRadiological EffluentTechnical Specifications forNuclearPowerPlants,"October1978;theseveralRegulatory Guidesreferenced inthesedocuments; and,communication withtheNRCstaff.Section5containsadetaileddescription oftheRadiological

.Environmental Monitoring,(REM) samplinglocations.

Shoulditbenecessary torevisetheODCM,theserevisions wi11bemadeinaccordance withTechnical Specifications.

'pItI'0IIHg

2.0 LIQUIDEFFLUENTS

2.1SetpointDeterminations 2.1.1BasisMonitorsetpoints willbeestablished suchthattheconcentration ofradionuclides intheliquideffluentreleasesinthedischarge canalwillnotexceedthoseconcentrations as-specified in10CFR20,Appendix8,TableII,Column2.Setpoints fortheServiceHaterSystemEffluentLinewillbecalculated quarterly basedontheradionuclides identified duringthepreviousyear'sreleasesfromtheliquidradwastesystemortheisotopesidentified inthemostrecentradwasteIreleaseorotheridentified probablesource.Setpoints fortheLiquidRadwasteEffluentLinewillbebasedontheradionuclides identified ineachbatchofliquidwastepriortoitsrelease.Afterrelease,theLiquidRadwastemonitorsetpointmayremainasset,orrevertbacktoasetpointbasedonaprevious<;-Semi-Annual, Radioactive EffluentReleaseReport,orinstallblankflangeinthedischarge lineanddeclareinoperable inaccordance withthetechnical specification.

SincetheServiceHaterSystemeffluentmonitorandLiquidRadwasteeffluentmonitorcanonlydetectgammaradiation, the.alarmsetpoints arecalculated byusingtheconcentration ofgammaemittingisotopesonly(orthecorresponding MPCvaluesforthesameisotopes, whichever arehigher)intheX>(uC1/mi)i>

expression (Section2.1.2,2.1.3).

0kj'-,lIPh'LIll4v'h(\~T~t.+fI+y4g~~~q+~fCal44 2.1.1(Cont'd)TheRequiredDilutionFactoriscalculated usingconcentrations ofallisotopespresent(orthecorresponding HPCvaluesfor-thesameisotopes, whichever arehigher)including tritiumand'othernon-gamma emitterstoensurethatallradionuclides inthedischarge canaldonotexceed10CFR20limits~2.1.2.::-Service WaterSystemEffluentLineAlarmSetpointThedetailedmethodsforestablishing setpoints fortheServiceWaterSystemEffluentLineMonitorshallbecontained intheNineMilePointStationProcedures.

Thesemethodsshallbeinaccordance withthefollowing:

~Setpoint(Hialarm)<0.9 Setpoint(Alertalarm)<6.7 (uC1/m1>sy

<CF)lTDF/Fsw2-[(uCi/ml)iT/MPCi]

il(UCi/ml)i~

(CF)TOF/FswZ;[(uCi/ml)iT/HPCi]

+background

+background (uCi/ml)ig concentration ofgammaemittingisotopeiinthesample,orthe.."-.-'corresponding MPCof,gammaemittingisotopei(HPC)ig,whichever ishigher(unitsuCi/ml).(uCt/ml)iT concentration ofanyradioactive isotopeiinthesampleincluding tritiumandothernon-gamma emittersorcorresponding MPCofisotopei,MPCi,whichever ishigher(unitsuCi/ml).'OF.'TotalOilutionFlow(unitsgallons/min)

FswCFHPCiServiceWaterFlow(unitsgallons/min) monitorcalibration factor(unitsnetcpm/uCi/ml) liquideffluentradioactivity concentrations limitforradionuclide iasspecified in10CFR20,AppendixB,TableII,Column2.

4<<~65~1q~~

2.1.2(Cont'd)Sample(MPC)i0.9and0.7[(uCi/ml)iT/MPCi]

TDF/FswThosenuclidespresentinthepreviousbatchreleasefromtheliquidradwasteeffluentsystemorthosenuclidespresentinthelastSemi-annual Radioactive EffluentReleaseReport(unitsuCi/ml)orthosenuclidespresentintheservicewatersystem.**

sameasMPCibutforgammaemittingnuclidesonly.factorsofconservatism toaccountforinaccuracies.

RequiredDilutionFactor.IfMPCvaluesareusedintheZ(uCi/ml)i y,theymustalsobeusedincalculating ROF(numerator).

ActualDilutionFactor2.1.3LiquidRadwasteEffluentLineAlarmSetpointThe;detailed methodsforestablishing setpoints fortheLiquidRadwaste'ffluentLineMonitorshallbecontained intheNineMilePointStationProcedures.

Thesemethodsshallbeinaccordance withthefollowing:

Setpoint(Hi-Hialarm)<0.9(uCi/ml)ig (CF)Setpoint(Hialarm)<0.7(uCi/ml)ig (CF)TDF/Fre[(uCi/ml)iT/MPC

]TDF/FreZ;[(uCi/ml)iT/HPCi]

background

+background (uCi/ml)i yconcentration ofgammaemittingisotopeiinthesampleor,thecorresponding MPCofgammaemittingisotopei(HPC)i."whichever ishigher.(uCi/ml)iT concentration ofanyradioactive isotopeiinthesampleincluding tritiumandothernon-gamma emittersorthecorresponding HPCofisotopeiHPCiwhichever ishigh'er.(unitsuCi/ml)TDFFreCFTotalDilutionFlow(unitsgallons/min)

.Radwaste EffluentFlow(unitsgallons/min) monitorcalibration factor(unitsnetcps/uCi/ml)

    • ForperiodswithknownreactorwatertoRCLCsystemleakage,RCLCmaximumpermissible concentration maybeprudently substituted fortheabove.

4.C(I Mpci(HPC)i.0.9and0.7liquideffluentradioactivity concentration limitforradionuclide iasspecified in10CFR20,AppendixB,TableII,Column2,forthosenuclidesdetectedbyspectralanalysisofthecontentsoftheradwastetankstobereleased.

(unitsuCi/ml)sameasHPCibutforgammaemittingnuclideonly.factorsofconservatism toaccountforinaccuracies.

X;[(uCi/ml)iT/HPCi]

RequiredDilutionFactor.IfHPCvaluesareusedintheX(uCi/ml)ix',

theymustalsobeusedincalculating RDF(numerator).

Notes:(a)

IfTDF/Fregf(uCi/ml)iT/MPCi]

thedischarge couldnotbemade,sincethemonitorwouldbecontinuously inalarm.Toavoidthissituation, Fwillbereduced(normally byafactorof2)toallowsettingthealarmpointataconcentration higherthantankconcentration.

Thi's.wil.lalso'resultinadischarge canalconcentration atapproximately 50Kmaximumpermissible concentration.

(b)ThevalueusedforTDFwillbereducedbythefractional quantity(1-FT),.whereFTis,tempering fraction(i.e.,diversion ofsomefractionofdischarge flowtotheintakecanalforthepurposeoftemperature control).

8+4%II'trf~x.C' 2.1.4Discussion 2.1.4.1ControlofLiquidEffluentBatchDischarges AtNineMilePointUnit1LiquidRadwasteEffluents arereleasedonly'nabatchmode.Topreventtheinadvertent releaseofanyliquidradwasteeffluents, radwastedischarge ismechanically isolated(blankflangeinstalled ordischarge valvechain-locked closed)following thecompletion ofabatchreleaseorseriesofbatchreleases.

,Thismechanical isolation remainsinplaceandwillonlyberemovedpriortothenextseriesofliquidradwastedischarges afterallanalysesrequiredinstationprocedures andTechnical Specification Table4.6.15-1A areperformed andmonitorsetpoints havebeenproperlyad]usted.

2.1.4.2Simultaneous Discharges ofRadioactive Liquids..'<<"If.duringthedischarge ofanyliquidradwastebatch,thereisanindication thattheservicewatercanalhasbecomecontaminated (throughaservicewatermonitoralarmorthroughagrabsampleanalysisintheeventthattheservicewatermonitorisinoperable) thedischarge shallbe.terminated immediately.

Theliquidradwastedischarge shallnotbecontinued untilthecauseoftheservicewateralarm(orhighgrabsampleanalysisresult)hasbeendetermined andtheappropriate corrective measurestakentoensure10CFR20,Appendix8,TableII,Column2(Technical Specification Section3.6.15.a(1))

limitsarenotexceeded.

ALi/A~

2.1.4.3SamplingRepresentativeness ThissectioncoversTechnical Specification Table4.6.15-1Notebconcerning thoroughly mixing'feachbatchofliquidradwastepriortosampling.

LiquidRadwasteTanksscheduled fordischarge atNineMilePointUnit1are'isolated (i.e;inletvalves:marked up)and.-at.leasttwo,tankvolumesofentrained fluidsarerecirculated priortosampling.

Minimumrecirculation timeiscalculated asfollows:-MinimumRecirculation Time2.0(T/R)Hhere:2.0Plantestablished mixingfactor,unitlessTankvolume,galRecirculation flowrate,gpm.Additionally.

theHiAlarmsetpointoftheLiquidRadwasteEffluentRadiation Monitorissetatavaluecorresponding tonotmorethan--""'.70'Lof-~itscalculated responsetothegrabsampleorcorresponding MPCvalues.Thus,thisradiation monitorwillalarmifthegrabsample,orcorresponding MPCvalue,issignificantly lowerinactivitythananypartofthetankcontentsbeingdischarged.

IWl*A'IO'"S~'omagr~'P(~,,~~~~i~)r+

k'g4>i'I 2.1.4.4LiquidRadwasteSystemsOperation Technical Specification 3.6.16.arequiresthattheliquidradwastesystemshallbeusedtoreducetheradioactive materials inliquidwastespriortotheirdischarge, asnecessary, tomeettheconcentration anddoserequirements ofTechnical Specification 3.6.15.Utilization of-theradwaste"system willbebasedonthecapability oftheindicated components ofeachprocesssystemtoprocesscontentsoftherespective lowconductivity andhighconductivity collection tanks:1)LowConductivity (Equipment Drains):RadwasteFilterandRadwasteDemin.(SeeFig.B-1)2)HighConductivity (FloorDrains):HasteEvaporator (seeFig.B-1)Cumulative dosecontributions fromliquideffluents forthecurrentl-'alendar

'quarterandthecurrentcalendaryearshallbedetermined asdescribed inSection2.3ofthismanualpriortothereleaseofeachbatchofliquidwaste.Thissamedosepro]ection ofSection2.3willalsobeperformed intheeventthatuntreated liquidwasteis.discharged, toensurethat.thedoselimits'of.Technical Specification 3.6.15.a(2) arenotexceeded.

(Therebyimplementing therequirements of10CFR50.36a, GeneralDesignCriteria60ofAppendixAandtheDesignOb)ective giveninSectionII-DofAppendixIto10CFR50).

~P1"J~W+

2.1.4.4(Cont'd)Forthepurposeofdosepro]ection, thefollowing assumptions shallbemadewithregardto-concentrations ofnon-gamma emittingradionuclides subsequently analyzedoff-site:

a)[H-3]>H-3Concentration foundrecentcondensate storagetankanalysis.

b)[Sr-89]>4xCs-137Concentration c)[Sr-90]>0.5xCs-137Concentration d)[Fe-55]>1xCo-60Concentration AssumedScalingFactorsusedinb,c,anddaboverepresent conservative estimates derivedfromanalysisofhistorical datafromprocesswastestreams.Following receiptofoff-siteH-3,Sr-89,Sr-90andFe-55analysisinformation, doseestimates shallberevised---usingactualradionuclide concentrations andactualtankvolumesdischarged.

Fp,cyb)}I',t'i,j>p<,pgb~iwp4'"r

  • e'I 2.1.4.5ServiceWaterSystemContamination Servicewaterisnormallynon-radioactive.

Ifcontamination issuspected, asindicated bya.significant increaseinservicewatereffluentmonitorresponse, grabsampleswillbeobtainedfromtheservicewaterdischarge linesandagammaisotopicanalysismeetingtheLLOrequirements ofTechnical Specification Table4.6.15-1completed.

Ifit-'is-determined.

thataninadvertent radioactive discharge isoccurring fromtheservicewatersystem,then:a)A50.59safetyevaluation shallbeperformed (ref.IEEBulletin80-10),b)Oailyservicewatereffluentsamplesshallbetakenandanalyzedforprincipal gammaemittersuntilthereleaseisterminated, c)Anincidentcomposite shallbepreparedforH-'3,grossalpha,Sr-89,Sr-90andFe-55analysesandI-'d)"Ooseprojections shallbeperformed

.inaccordance withSection2.3ofthismanual(usingestimated concentrations forH-3,Sr-89,Sr-90andFe-55tobeconservatively determined bysupervision atthetimeoftheincident).

Additionally, servicewatereffluentmonitorsetpoints mayberecalculated usingtheactualdistribution ofisotopesfoundfromsampleanalysis.

1I~LgC4t*'AtttEI'E 2.2LiquidEffluentConcentration Calculation Thiscalculation documents compliance withTechnical Specification Section3.6.1.5.a (1).Theconcentration ofradioactive materialreleasedinliquideffluents tounrestricted areas(seeFigureB-7)shallbelimitedtothe'concentrations specified in10CFR20,AppendixB,TableII,Column2,forradionuclides otherthandissolved orentrained noblegases.Fordissolved orentrained noblegases,theconcentration shallbelimitedto2E-4microcurie/milliliter (uCi/ml)totalactivity.

Theconcentration ofradioactivity fromLiquidRadwastebatchreleasesand,ifapplicable, ServiceHaterSystemandemergency condenser start-upventdischarges areincludedinthecalculation.

Thecalculation isperformed foraspecificperiodoftime.Nocredittakenforaveraging overthecalendaryearaspermitted by10CFR20.106.

Thelimitingconcentration iscalculated asfollows:~PCFrti"11<~s(("i/ml)is*Fs)/(

Pi*Zs(FsHhere:HPCFractionThelimitingconcentration of10CFR20,Appendix8,TableII,forradionuclides otherthandissolved orentrained noblegases.Fornoblegases,theconcentration shallbelimitedto2E-4microcurie/ml totalactivity.

IV@.1,,S'IlkWih~ptertI.gkA~~

2.2(Cont'd)(uCi/ml)i Theconcentration ofnuclideiinparticular iseffluentstreams,uCi/ml.FTheflowrateofaparticular effluentstreams,gpm.MPCiThelimitingconcentration ofaspecificnuclideifrom.'10CFR20, Appendixb,Table-II,Column2(noblegaslimitis2E-4uCi/ml)X((uCi/ml)i

  • F)Thetotalactivityrateofnuclidei,inalleffluentstreamss,uCi/ml*gpm

$(F)".Thetotalflowrateofalleffluentstreamss,gpm(including thosestreamswhichdonotcontainradioactivity).

AvalueoflessthanoneforMPCfractionisconsidered acceptable forcompliance withTechnical Specification Section3.6.15.a.(1).

2.3DoseDetermination

-,2.3.1,MaximumDoseEquivalent PathwayAdoseassessment reportwaspreparedfortheNineMilePointUnit1facilitybyCharlesT.Main,Inc.,ofBoston,MA.Thisreportpresented thecalculated doseequivalent ratestoindividuals aswell,asthe.,population withina50-mileradiusofthefacilitybasedontheradionuclides releasedin-liquid.and=gaseous effluents-during.

thetimeperiodsof1July1980through31December1980andfromJanuary1981through31December1981;Theradwasteliquid'releases arebasedonacanaldi.scharge rateof590ft/secwhichaffectsnearfieldandfarfielddilution; therefore, thisreportisspecifictothis.situation.

Utilizing theeffluentdatacontained inthe12 rPAg4J<7 2.3.1(Cont'd)Semi-Annual Radioactive EffluentReleaseReportsassourceterms,doseequivalent ratesweredetermined usingtheenvironmental pathwaymodelsspecified inRegulatory Guides1.109and1.111asincorporated intheNRCcomputercodesLADTAPforliquidpathways, andXOQDOQandGASPARforgaseouseffluentpathways.

Doseequivalent rateswere-calculated forthe'total'ody aswellassevenorgansand/ortissues---

fortheadult,teen,child,andinfantagegroups.Fromthestandpoint ofliquideffluents, thepathwaysevaluated includedfishanddrinkingwateringestion, andexternalexposuretowaterandsediment.

Themajorityofthedoseforaradwasteliquidbatchreleasewasreceivedviathefishpathway.However,tocomplywithTechnical Specifications fordoseprojections, thedrinkingwaterandsedimentpathwaysareincluded.

Therefore, alldosesdueto-liquideffluents arecalculated monthlyforthefishanddrinkingwateringestion pathwaysandthesedimentexternalpathwayfromalldetectednuclides"<<inliquideffluents releasedtotheunrestricted areastoeachorgan.Thedoseprojection forliquidbatchreleaseswillalsoincludedischarges fromtheemergency condenser ventasapplicable, forallpathways.

Eachagegroupdosefactor,Ait,isgivenintables1-1to1-8.Toexpeditetime the,doseiscalculated foramaximumindividual insteadofeachagegroup.Thismaximumindividual willbeacomposite ofthehighestdosefactorofeachagegroupforeachorgan,henceAit.Thefollowing expression fromNUREG0133,Section4.3isusedtocalculate dose:Dtgi[Alt$1(dT1CilF1)]

13

  • W~hII+'Igc~4.

2.3.1(Cont'd)Nhere:OtThecumulative dosecommitment tothetotalbodyoranyorgan,fromtheliquideffluents forthetotaltimeperiod(dT1),mremdT1Thelengthofthe1thtimeperiodoverwhichCilandFlareaveragedforallliquidreleases, hoursCilTheaverageconcentration ofradionuclide, i,inundiluted liquideffluents duringtimeperioddT1fromanyliquidrelease,uCi/mlAitThesiterelatedingestion dosecommitment factortothetotalbodyoranyorgantforeachidentified principal gammaorbetaemitterforamaximumindividual, mrem/hrperuCi/mlFlThenearfieldaveragedilutionfactorforCilduringanyliquideffluentrelease.Definedastheratioofthemaximumundiluted liquidwasteflowduringreleasetothe.averageflowfromthesitedischarge structure tounrestricted receiving waters,unitless.

Aitvaluesforradwasteliquidbatchreleasesatadischarge rateof295ft/sec(onecirculating waterpumpinoperation) arepresented intable's1-1to1-4.Aitvaluesforanemergency iatcondenser ventreleasearepresented intables1-5to1-8.The'mergency condenser ventreleasesareassumedtotraveltotheperimeter drainsystemandreleasedfromthedischarge structure atarateof.33ft/sec.SeeAppendixAforthedosefactorAit3derivation.

Toexpeditetimethedoseiscalculated toamaximumindividual.

Thismaximumindividual isa;composite'of

-thehighest-."

dosefactorAitofeachagegroupaforeachorgantandeachnuclidei.Ifanuclide"is detectedforwhichafactorisnotlisted,thenitwillbecalculated andincludedinarevisiontotheOOCN.

f0i~i4,e+$'a,,C'(<>>5 Y"ztl$'~,

2.3.1(cont'd)Alldosescalculated inthismannerforeachbatchofliquideffluentwillbesummedforcomparison withquarterly andannuallimits,addedtothedosesaccumulated fromotherreleasesinthequarterandyearofinterest.

Inallcases,thefollowing relationships willhold:Foracalendarquarter:0t<1.5mremtotalbody0<5mremforanyorganForthecalendaryear:Ot<.3.0mremtotalbody0t<10mremforanyorgan-"<~where0'otal;dose receivedduetoliquideffluentreleasestothetotalbodyoranyorgan,

+pvEp1e 2.3.1(Cont'd)Iftheselimitsareexceeded, aspecialreportwillbesubmitted to-'theNRCidentifying

.the..cause,and,,proposed corrective actions.Inaddition, iftheselimitsareexceededbyafactoroftwo,calculations shallbemadetodetermine ifthedoselimitscontained in40CFR190havebeenexceeded.

Doselimits,ascontained in40CFR190aretotalbodyandorgandosesof25mremperyearandathyroiddoseof75mremperyear.=Thesecalculations willincludedosesasaresultofliquidandgaseouspathwaysaswellasdosesfromdirectradiation.

Theliquidpathwayanalysiswillonlyincludethefishandsedimentpathwayssincethedrinkingwaterpathwayisinsignificant.

Thispathwayis.onlyincludedinthe.station's effluentdoseprojections tocomply'""withTechnical Specifications.

Liquid,gaseousanddirectradiation.

pathwaydoseswillconsidertheJamesA.FitzPatrick andNineMilePointUnitIIfacilities aswellasNineMilePointUnitINuclear.Station.Intheeventthecalculations demonstrate thatthe40CFR190doselimits,asdefinedabove,havebeenexceeded, thenareportshallbepreparedandsubmitted totheCommission within30daysasspecified inSection3.6.15.doftheTechnical Specifications.

I'"",i.'Section, 4.,0'oftheODCMcontainsmoreinformation concerning calculations foranevaluation ofwhether40CFR190limitshavebeenexceeded.

I.~01C.aI*)It1l'E

3.0 GASEOUSEFFLUENTS

3.1SetpointDeterminations 3.1.1Basis~~Stackgasandoffgasmonitorsetpoints willbeestablished suchthattheinstantaneous releaserateofradioactive materials ingaseouseffluents doesnotexceedthe10CFR20limitsforannualrelease.rate.Thesetpoints willbeactivated iftheinstantaneous doserateator-beyondthe(land)site'boundary would.exceed500mrem/yr,to.the..wholebodyor3000mrem/yrtotheskinfromthecontinuous releaseofradioactive noblegasinthegaseouseffluent.

Emergency condenser ventmonitorsetpoints willbeestablished such"thatthereleaserateforradioactive materials ingaseouseffluents donotexceedthe10CFR20limitsforannualreleaserateovertheprojected longestperiodofrelease.Monitorsetpoints fromcontinuous releasepointswillbedetermined onceperquarterundernormalreleaserateconditions andwillbebasedon'the'isotopic composition oftheactualreleaseinprogress, oranoffgasisotopicdistribution oramoreconservative defaultcomposition specified inthepertinent procedure.

Ifthecalculated setpointtshigherthantheexistingsetpoint, itisnotmandatory thatthesetpointbechanged.Monitorsetpoints foremergency condenser ventmonitorsareconservatively fixedat5mr/hrforreasonsdescribed inSections3.1.4andtherefore donotrequireperiodicrecalculations.

Underabnormalsitereleaserateconditions, monitor.alarmsetpoints.

fromcontinuous releasepointswillberecalculated and,ifnecessary, resetatmorefrequentintervals asdeemednecessary by.CORMSupervision.

Inparticular, contributions frombothJAFandNMP-2andtheEmergency Condenser Ventsshallbeassessed:

"Duringoutagesanduntilpower.operation isagainrealized, thelastoperating stackandoffgasmonitoralarmsetpoints shallbeused.

k7i'tZF<~P 3.1.1(Cont'd)Sincemonitorsrespondtonoblegasesonly,monitoralarmpointsaresettoalarmpriortoexceeding thecorresponding totalbodydose'rates.Theskindoseratelimitisnotusedinsetpointcalculations becauseitisneverlimiting.

3.1..2,StackMonitorSetpoints Thedetailedmethodsforestablishing setpoints shallbecontained inthestationprocedures.

Thesemethodsshallapplythefollowing generalcriteria:

(1)Rationale forStackmonitorsettingsisbasedonthegeneralequation:

releaserateactualcorresponding doserate,actualreleaseratemax.allowable corresponding doserate,max.allowable

()max500mrem/yrwhere:Vireleaserateforeachisotopei,uCi/secgamma'hole bodydosefactorinunitsofmrem/yrperuCi/sec(SeeTable3-2)(Q)maxinstantaneous releaseratelimituCi/sec18

+a'v'1~IIQ%ltl 3.1.2(Cont'd)(2)Toensurethat10CFR20andTechnical Specifications doseratelimitsarenotexceeded, thehihialarmsonthestackmonitorsshallbesetlowerthanorequalto(0.9)(Q).Hialarmsmax'hallbesetlowerthanorequalto(0.5)(Q)max'3)Basedontheaboveconservatism, thedosecontribution fromJAFandNMP-2canusual,lybeignored..DuringEmergency Classifications atJAForNMP-2duetoairborneeffluent, orafteremergency

.condenser vent;releases

.of-significant proportions, the500mrem/yrvaluemaybereducedaccordingly.

(4)ToconvertmonitorgrosscountratestouCi/secreleaserates,thefollowing generalformulashallbeapp'lied:

(C-B)KQuCi/secreleaseratewhere:'BKsCmmonitorgrosscountrateincpsorcpm;cpscountspersecond,cpmcountsperminutemonitorbackground countratestackmonitorefficiency factorwithunitsofuCi/sec-cps oruCi/sec-cpm (5)MonitorKfactorsshallbedetermined usingthegeneralformula:KQiQi/(C-8)where:individual radionuclide stackeffluent.releaserateasdetermined byisotopicanalysis.

Kfactorsmoreconservative thanthosecalculated bythe-abovemethodology maybeassumed.-19

,bt'4r~II4U 3.1.2(Cont'd)Alternatively, whenstackreleaseratesarenearthelowerlimitofdetection, thefollowing generalformulamaybeused.tocalculate k:1/KsE~(ii~kYkEk)3.7E4dff'-uCiwhere:fstackflowincc/secEefficiency inunitsofcpm-cc/uCi orcps-cc/uCi (cpmcountsperminute;cpscountspersecond)Ekcpm-cc/bps orcps-cc/psFromenergycalibration curveproducedduringNBStraceable primarygascalibration ortransfersourcecalibration (bpsbetapersecond;psgammaspersecond)Ykb/d(betas/disintegration) orV/d(gammas/d)

FiActivityfractionofnuclideiinthemixtureinuclidecounterk.discreteenergybetaorgammaemitterpernuclidecountersi~secondsThismonitorcalibration methodassumesanoblegasdistribution typicalofarecoilreleasemechanism.

Toensurethatthecalculated efficiency isconservative, betaorgammaemissions whoseenergyisabovetherangeofcalibration ofthedetectorarenotincludedinthecalculation.

Q}4 3.1.3Recomb)ner Discharge

<DffGas)MonitorSetpoints (1)Thehihialarmpointsshallactivatewithrecombiner discharge ratesequaltoorlessthan500,000uCi/sec.Thisalarmpointmaybesetequal-.to orlessthan1Ci/secforaperiodoftimeInottoexceed60daysprovidedtheoffgastreatment systemisinoperation.

(2)Thehialarmpointsshallactivatewithrecombiner discharge ratesequaltoorlessthan500,000uCi/sec(3)ToconvertmonitormR/hrreadingstouCi/sec,theformulabelowshallbeapplied:<R)(KR)QRuCi/secrecombiner discharge releaserate"where:RmR/hrmonitorindicator KRefficiency factorinunitsofuCi/sec/mR/hr determined priortosettingmonitoralarmpoints(4)MonitorKRfactorsshallbedetermined usingthegeneralformula:KRQi/Rwhere:Qi-individual radionuclide recombiner discharge releaserateasdetermined byisotopicanalysisandflowratemonitor.KRfactorsmoreconservative thanthosecalculated bytheabovemethodology maybeassumed.

J4jCIf4/Qi'lag'I~ppAl 3.1.3(Cont'd)(5)Thesetpoints chosenprovideassurance thatthetotalbodyexposuretoanindividual attheexclusion areaboundarywillnotexceedaverysmallfractionofthelimitsof10CFRPart100intheeventthiseffluentisinadvertently discharged directlytotheenvironment withouttreatment (therebyimplementing therequirements ofGeneralOesignCriteria60and64ofAppendixAto10CFRPart,50)..Additionally, thesesetpoints serveto,limitbuildupoffissionproductactivitywithinthestation.systemswhichwouldresultifhighfuelleakageweretobepermitted overextendedperiods.3.1.4Emergency Condenser VentHonitorSetpointThemonitorsetpointwasestablished bycalculation

("Emergency

,Condenser VentHonitorAlarmSetpoint",

January13,1986,NHPCFileCode¹'l61*99).

Assumingahypothetical casewith(1)reactorwatertiodineconcentrations higherthantheTechnical Specification Limit,(2)reactorwaternoblegasconcentrations higherthanwouldbeexpectedatTechnical Specification iodinelevels,and(3)leakageofreactorsteamintotheemergency condenser shellat300'Aofratedflow(or1.3E6lbs/hr),thecalculation predictsanemergency condenser ventmonitorresponseof20mR/hr.Suchareleasewouldresultinlessthan'0CFR20.doseratevaluesatthesiteboundaryandbeyondfortypical"emergency condenser cooldownperiods.Sincea20mR/hrmon'itorresponsecan,intheory,beachievable onlywhenreactorwateriodinesarehigherthanpermitted byTechnical Specifications, aconservative monitorsetpointof5mr/hrhasbeen-adopted.

IICof~hVWII,aITWIr'Tr~'t.ITl\ITttI0 3.1.5Discussion 3.1.5.1StackEffluentMonitoringSystemDescription

-TheNMP-1Stack'EffluentaMonitoring Systemconsistsoftwosubsystems; theRadioactive GaseousEffluentMonitoring System(RAGEMS)andtheoldGeneralElectricStackMonitoring System(OGESMS).

Duringnormaloperation, theOGESMSshallbeusedtomonitorstationnoble'aseffluents andcollectparticulates andiodinesamplesincompliance withTechnical Specification requirements.

TheRAGEMS.is designedtobepromptlyactivated fromtheMainControl"Roomforuseinhighrangemonitoring duringaccidentsituations incompliance withNUREG0737criteria.

Overallsystemschematic fortheOGESMSandRAGEMSareshownonFigureB-9.Asimplified viewofRAGEMSShowingUnit0,1,2,3and4canbefoundonFigureB-S.TheRAGEMScanprovidecontinuous accidentmonitoring andon-lineisotopicanalysisofNMP-1stackeffluentnoblegasesatLowerLevelsofDetection lessthanTechnical Specification Table4.6.15-2limits.Activities aslowas5.0E-Bandashighas2.0E5uCi/ccfornoblegasesaredetectable bythesystem.

i&jan"JP~.0-y~yII~*'Iletgledbl4II 3T.5.2StackSampleflowPath-RAGEHS'"Theeffluentsampleisobtainedinsidethestackatelevation 530'singanisokinetic probewithfourorifices.

Thesamplelinethenbendsradiallyoutandbackintothestack;descendsdownthestackandoutofthestack-atapproximately elevation 257';runshorizontally (enclosed inheattracing)some270'longtheoffgas.tunnel;andenterstheRAGEHSlocatedontheTurbineBuilding250'Dilution cabinet-Unit0)andOffGasBuilding247'Particulate, Iodine,NobleGasstations-Units1-3).'Inthe'Dilution cabinet'of theRAGEHS,thestackgasmaybedilutedduringaccidentsituations approximately 100-200X(firststage)or10000-40000 X(firstandsecondstage)withgaseousnitrogensuppliedfromanon-siteliquidnitrogenstoragetank(seeFigure8-9).FromUnit0,thesamplegasentersUnit1-3ofRAGEHSandflowsthruin-lineparticulate andiodinecartridges andthenthrueithera6liter(lowrange)or30cc(highrange)noblegaschamber.ThesamplegasnextflowsbackthruUnit0andtheoffgastunnel;andbackintothestack.

I1+4gVL41wpfTJ'1SktI' 3.1.5.3StackSampleFlowPath-OGESHSTheOGESHSsampleisobtainedfromthesamestacksampleprobeastheRAGEHS.Fromtheexitofthestackatelevation 257',thesamplelinerunseastapproximately 20'ndthenvertically approximately 8'otheOGESMSskid.IntheOGESMS,sampleflowsthruaparticuate/,

.iodinecartridge housingand.fournoblegasscintillation detectors (i.e..07and08lowrange-beta detectors andRN-03AandRN-038highrangegammadetectors).

FromOGESHS,thestacksampleflowsbackintothestackatapproximately elevation 257'.AllOGESMSdetectoroutputsaremonitored andrecordedremotelyintheHainControlRoom.Alarmingcapabilities areprovidedtoalertOperators ofhighreleaserateconditions priortoexceeding Technical Specification 3.6.15.b(1)adoseratelimits.,Stackparticulate andiodinesamplesareretrieved manuallyfromtheOGESMSandanalyzedinthelaboratory usinggammaspectroscopy atfrequencies andLLOsspecified inTable4.6.15-2oftheTechnical Specifications.

I'tI*P'tF 3.1.5.4SamplingFrequency/Sample AnalysisRegardless ofwhichstackmonitoring subsystem isutilized, radioactive gaseous"wastes

.shallbesampledandanalyzedinaccordance withthesamplingandanalysisprogramspecified inTechnical Specification Table4.6.15-2.

Particulate samplesaresavedandanalyzedforprincipal gammaemitters, grossalpha,Fe-55,Sr-89,Sr-90atmonthlyintervals minimally.

Thelatterthreeanalysesareperformed off-sitefromacomposite sample.Sampleanalysisfrequencies areincreased duringelevatedreleaserateconditions, following startup,shutdownandinconjunction witheachdrywellpurge.Consistent withTechnical Specification Table4.6.15-2, stackeffluenttritiumissampledmonthly,duringeachdrywellpurge,and.weeklywhenfuelisoffloadeduntilstablereleaseratesaredemonstrated.

Samplesareanalyzedoff-site.

Linelosscorrection factorsareappliedtoallparticulate and"*"i,iodine.results.-Correction factorsof2.0and1.5areusedfordataobtainedfromRAGEHSandOGESHSrespectively.

Thesecorrection factorsarebasedonempirical datafromsamplingconducted atNHP-1in1985(memofromJ.BlasiaktoRAGEHSFile,1/6/86,"StackSampleRepresentativeness Study:RAGEHSvs.In-StackAuxiliary ProbeSamples").

~k(1I~'i 3.1.5.5I-133Estimates Monthly,thestackeffluentshallbesampledforiodinesovera24hourperiod-andtheI-135/I-131,and theI-133/I-131 ratioscalculated.

Theseratiosshallbeusedtocalculate I-133,I-135releaseforlongeracquisition samplescollected duringthemonth.Additionally, theI-135/I-131 andI-133/I-131 ratiosshouldalsobedetermined afterasignificant change-intheratioissuspected (eg,plantstatuschangesfromprolonged shutdowntopoweroperation orfueldamagehasoccurred).

3.1.5.6GaseousRadwasteTreatment SystemOperation Technical Specification 3.6.16.brequiresthatthegaseousradwastetreatment systemshallbeoperableandshallbeusedtoreduceradioactive materials ingaseouswastepriortotheirdischarge asnecessary tomeettherequirements ofTechnical Specification 3.6.15.b.

ToensureTechnical Specification 3.6.15.blimitsarenotexceeded, andtoconfirmproperradwastetreatment systemoperation asapplicable, cumulative dosecontributions forthecurrentcalendarquarterandcurrentcalendaryearshallbedetermined monthlyinaccordance withsection3.2ofthismanual.Initialdosecalculations shallincorporate.

thefollowing-assumptions with,regardtoreleaseratesofnon-gamma emittingradionuclides subsequently analyzedoff-site:

$l4gP">>'"wh'w'N~y'~~

~'oi"pt, 3.1.5.6(Cont'd)a)H-3releaserate24uCi/secb)Sr-89releaserateZ4xCs-137releaseratec)Sr-90releaserateZ0.5xCs-137releaserated)Fe-55releaserate21xCo-60releaserateAssumedreleaseratesrepresent conservative estimates derivedfromanalysisofhistorical datafromeffluentreleasesandprocesswastestreams(SeeNAP34023,C.HaretoJ.Blasiak,April29,1988,"DoseEstimates forBeta-Emitting Isotopes"

).Following receiptofoff-siteH-3,Sr-89,Sr-90,,Fe-55 analysisinformation, doseestimates shallberevisedusingactualradionuclide concentrations.

3.2DoseandDoseRateDeterminations Inaccordance withspecifications 4.6.15.b.

(1),4.6.15.b.

(2),and4.6.15.b.(3) doseanddoseratedeterminations willbemademonthlytodetermine:

(1)TotalbodydoseratesandgammaairdosesatthemaximumX/Q'landsectorsiteboundaryinterface andbeyond.(2)Skindoseratesandbetaairdosesatthe.maximumX/Qlandsectorsite'boundary interface andbeyond.(3)ThecriticalorgandoseanddoserateatthemaximumX/Qlandsectorsiteboundaryinterface andatacriticalreceptorlocationbeyondthesiteboundary..

28

'pEv 3.2(Cont'd)Averagemeteorological data(ie,maximumfiveyearannualaverageX/QandD/Qvaluesinthecaseofelevatedreleasesor1985annualaverageX/QandD/Qvalues,inthecaseofgroundlevelreleases) shallbeutilizedfordoseanddoseratecalculations.

Whereaveragemeteorological dataisassumed,doseanddoseratesduetonoblegasesatlocations beyondthesiteboundarywillbelowerthanequivalent siteboundarydose-anddoserates.Therefore, undertheseconditions, calculations ofnoblegasdoseanddoseratesbeyondthemaximumX/Qlandsectorsiteboundarylocations canbeneglected.

Thefrequency ofdoseratecalculations willbeupgradedwhenelevatedreleaserateconditions specified insubsequent sections3.2.1.1and3.2.1.2arerealized.

rEmergency condenser ventreleasecontributions tothemonthlydoseanddoseratedeterminations willbeconsidered onlywhentheemergency condenser returnisolation valveshavebeenopenedforreactorcooldownorifEmergency Condenser tubeleaksdevelopwithorwithoutthesystem'sreturnisolation valveopened.Withouttubeleakageoropeningofthereturnisolation valves,releasesfromthissystemarenegligible andthecorresponding dosecontributions donothavetobeincluded.

I I*me'q<a<~"<~,q"".'ltFgv, 3.2(Cont'd)Hhenreleasesfromtheemergency condenser haveoccurred, doserateanddosedeterminations shall'beperformed usingmethodology in3.2.1and3.2.2.Furthermore, environmental samplingmayalsobeinitiated torefineanyactualcontribution todoses.SeeSection3.4.Criticalorgandoses.anddoseratesmaybeconservatively calculated..

byassuming.theexistence ofamaximumindividual.

Thisindividual isacomposite ofthehighestdosefactorofeachagegroup,foreachorganandtotalbody,andeachnuclide.Itisassumedthatallpathwaysareapplicable andthehighestX/Qand/or0/QvalueforactualpathwaysasnotedinTable3-1areineffect.Themaximumindividual's doseisequaltothesamedosethatpersonwouldreceiveiftheyweresimultaneously sub]ected tothehighestpathwaydoseateachcriticalreceptoridentified foreachpathway.Thepathwaysincludegrass-(cow andgoat)-milk, grass-cow-meat, vegetation, groundplaneandinhalation.

TocomplywithTechnical Specifications wewillcalculate themaximumindividual doserateatthesiteboundaryand"'eyondatthecriticalresidence.

Ifdoseordoseratescalculated, usingtheassumptions notedabove,reachTechnical Specification limits,actualpathwayswillbeevaluated, anddose/dose ratesshallbecalculated atseparatecriticalreceptorlocations andcomparedwithapplicable limits.30 ekedAI6'ltIII, 3.2.1DoseRate'ose'rateswillbe-calculated.

monthly,ataminimum,orwhentheHi-Histackmonitoralarmsetpointisreached,todemonstrate thatdoseratesresulting fromthereleaseofnoblegases,tritium,iodines,andparticultes withhalflivesgreaterthan8daysare'ithinthelimitsspecified inlOCFR.20.

Theselimitsare:NobleGasesHholeBodyDoseRate500mrem/yrSkinDoseRate3000mrem/yrTritiumIodinesandParticulates OrganDoseRate1500mrem/yr3.2.1.1NobleGasesThefollowing noblegasdoserateequationincludesthecontribution fromthestack(s)elevatedreleaseandtheemergency condenser vent(v)groundlevelreleasewhenapplicable (See.section3.2).31 Pf~

fortotalbodydoserates(mrem/sec):

ORg(mrem/sec)

-3.17E-8Zi.[ViQi,+Ki(X/Q)Qi]iiis'vivForskindoserates(mrem/sec):

OR~+8(mrem/sec)-

3.17E-8Zi[(Li(X/Q)s+1.118i)Qis+(Li+1.11Ni)<X/Q)vQiv~

where:OR~totalbodygammadoserate(mrem/sec).

OR~+6skindoseratefromgammaandbetaradiation (mrem/sec).

=='he.constant, accounting forthegammawholebodydoseratefromstackradiation, foranelevatedfiniteplumereleasesforeachidentified noblegasnuclide,i.ListedonTable3-2inmrem/yrperuCi/sec..

Kitheconstantaccounting forthegammawholebodydoseratefromimmersion inthesemi-infinite cloudforeachidentified noblegasnuclide,i.ListedinTable3-3inmrem/yrperuCi/m3(fromReg.Guide1.109)Qithereleaseofisotopei;(uCi;sstack,vvent).X/Q-therelativeplumeconcentration

<inunitsofsec/m3)atthelandsectorsiteboundaryorbeyond.'Averagemeteorological data(Table3-1)isused.'"Elevated" X/Qvaluesareusedforstackreleases(s",'stack);

"Ground"X/QvaluesareusedforEmergency Condenser Ventreleases(vvent).theconstantaccounting forthebetaskindoseratefromimmersion inthesemi-infinite cloudforeachidentified noblegasnuclide,i.ListedinTable3-3:inmrem/yrperuCi/m3(fromReg.Guide1.109),.theconstant.accounting for,the'airgammaradiation fromtheelevatedFiniteplumeresulting fromstackreleasesforeachidentified noblegasnuclide,i.ListedinTable3-2inmrad/yrperuCi/sec.Hitheconstantaccounting forthegammaairdoseratefrom-immersion inthesemi-infinite cloudforeachidentified noblegasnuclide,i.ListedinTable3-3inmrem/yrperuCi/m3(fromReg.Guide1.109)SeeAppendix8forderivation ofBi,andVi.32 srfP.Ag<

3.2.1.2Tritium,lodinesandParticulates Toensurethatthe'500'mrem/year sitedoseratelimitisnotexceeded, offsitedoseratesfortritium,iodineandparticulates withhalflivesgreaterthan8daysshallbecalculated monthlyandwhenreleaserates(Q).exceed0.34uCi/secusingthefollowing equation.

Oak(mrem/sec) 3.17E-8$~(~iRijak[Wsis+WvivWhere:oakTotaldosetoeachorgankofanindividual inagegroupa(mrem/sec).

dispersion parameter eitherX/Q(sec/m3)or0/Q(1/m2)depending onpathwayandreceptorlocationassumed.Averagemeteorological datais"used(Table3-1)."Elevated" W~valuesareusedforstackreleases(sstack);"Ground"WgvaluesareusedforEmergency Condenser Ventreleases(vvent).QiRi]ak3.17E-.Sthetotalquantityofisotopeireleased, (uCi/sec; sstack,vvent)thedosefactorforeachisotopei,pathway],agegroupa,andorgank(Table3-4,through3-22;m2-mrem/yr peruCi/secforallpathwaysexceptinhalation, mrem/yrperuCl/m3.theinverseofthenumberofsecondsinayear.,TheR.valuescontained inTables3-4through3-22.werecalculated usingthemethodology definedinNUREG-0133 andparameters fromRegulatory Guide1.109,Revision1;aspresented inAppendixC.When-thereleaserateexceeds0.34uCi/sec,thedoserateassessment shallalsoincludeJAFandNMP-2contribution.

33 Pp4SA+v,1<

Theuseofthe0.34uCi/secreleaseratethreshold toperformdoseratecalculations isjustified asfollows:(a)The1500mrem/yrorgandoseratelimitcorresponds toaminimumreleaseratelimitof0.34uCi/seccalculated usingtheequation:

1500(Q/sec)x(Ri)N))where:1500siteboundarydoseratelimit(mrem/year)

(Ri]"])max themaximumcurie-to-dose conversion factorequalto4.45E3mrem-sec/uCi-yr forSr-90,childboneatthecriticalresidence receptorlocationbeyondthesiteboundary.

(b)Theuseof0.34uCi/secreleaseratethreshold andthe4.45E3mrem-sec/uCi-yr curie-to-dose conversion factorisconservative sincecurie-to-dose conversion factorsforotherisotopeslikelytobepresentaresignificantly lower.

bfIs'4 3.2.2Dose-Calculations willbeperformed.

monthlyataminimum,.todemonstrate thatdosesresulting fromthereleaseofnoblegases,tritium,iodines,andparticulates withhalflivesgreaterthan8daysarewithinthelimitsspecified in10CFR50,AppendixI.Theselimitsare:NobleGases5mRgamma/calendar quarter'0mradbeta/calendar quarter10mRgamma/calendar year'0mradbeta/calendar yearTritiumIodinesandParticulates 7.5mremtoanyorgan/calendar quarter15mremtoanyorgan/calendar year l+%i'Id4II'PtI1' 3.2.2.1NobleGasAirDoseThefollowing NobleGasairdoseequationincludescontributions fromthestack(s)elevated.release.and theemergency condenser vent(v)groundlevelreleasewhenapplicable (seesection3.2):Forgammaradiation.

(mrad):Dg(mrd)317E8~iHi(XQ)vQiv+BiQisForbetaradiation (mrad):08(mrad)3.17E-SX)Ni(XQ)viv+siswhere:0ygammaairdose(mrad)0>betaairdose(mrad)theconstantaccounting fortheairgammaradiation fromtheelevatedfiniteplumeresulting fromstackreleasesforeachidentified noblegasnuclide,i.ListedinTable3-2inmrad/yr,peruCi/sec.NiTheconstantaccounting fortheairbetadosefromimmersion inthesemi-infinite cloudforeachidentified noblegasnuclide,i.ListedonTable3-3inmrad/yrperuCi/m3(fromReg.Guide1.109).Qithetotalquantityofisotopeireleased, (uCi/sec.)

NotethattheunitsforthegammaairdoseareinmradcomparedtotheunitsforthelimitsareinmR.TheNRCrecognizes that1mR1mrad,forgammaradi'ation.

36 4q(gi 3.17E-Stheinverseofthenumberofsecondsinayear.theconstantaccounting fortheairgammadosefromimmersion inthesemi-infini tecloudforeachidentified noblegasnuclide,i.ListedonTable3-3inmrad/yrperuCi/m3<fromReg.Guide1.109).Allotherparameters areasdefinedinsection3.2.1.1.3.2.2.2Tritium,IodinesandParticulates

'oensurethatthe15mrem/yrfacilitydoselimitisnotexceeded, offsitedosesfortritium,iodines,andparticulates withhalflivesgreaterthan8daysshallbecalculated monthlyusingthefollowing

.<<equation:

0ak(mrem)3.17E-8Z~(SiRi]akWsis+WvivWhere:0akWgQiRi~ak3.17E-8Totaldosetoeachorgankofanindividual inagegroupa(mrem).dispersion parameter eitherX/Q(sec/m3)or0/Q(1/m2)depending onpathwayandreceptorlocationassumed.Averagemeteorological dataisused(Table3-1)."Elevated" W~valuesareused.forstackreleases(sstack);"Ground"W~valuesareusedforEmergency Condenser Ventreleases(vvent).thetotalquantityofisotopeireleased,

<uCi/sec; s-stack,vvent)thedosefactorforeachisotopei,pathway],agegroupa,andorgank(Tables3-4,through3-22;m2-mrem/yr peruCi/sec)'theinverseofthenumberofsecondsinayear37 fII~0hlyCE' TheRvaluescontained inTables3-4through3-22werecalculated usingthemethodology definedinNUREG-0133 andparameters fromRegulatory Guide1.109,Revision1;aspresented inAppendixC.3.2.2.3Accumulating DosesDoseswillbecalculated monthly,ataminimum,forgammaair,betaair,andthecriticalorganforeachagegroup.Doseestimates will,also,becalculated monthlypriortoreceiptofanyoffsiteanalysisdatai.e.,strontium, tritium,andiron-55.Resultswillbesummedforeachcalendarquarterandyear.Thecriticaldosesarebasedonthefollowing:

noblegasplumeairdosedirectradiation fromgroundplanedeposition inhalation dosecowmilkingestion dosegoatmilkingestion dose'cowmeatingestion dosevegetation (foodcrops)ingestion doseThequarterly andannualresultsshallbecomparedtothelimitslistedinparagraph,3.2.2.

If,thelimitsareexceeded, specialreports,asrequiredbySection6.9.3oftheTechnical-Specification, shallbesubmitted.

38 A~"I 3.3CriticalReceptors Inaccordance withtheprovisions of10CFR20and10CFR50,AppendixI,thecriticalreceptors havebeenidentified andare"contained inTable3-1.Forelevatednoblegasreleasesthecriticalreceptoristhesiteboundary.

Hhen1985averageannualX/Qvaluesareusedforgroundlevelnoblegasreleases, thecriticalreceptoristhemaximumX/Qlandsectorsiteboundaryinterface.

Fortritium,iodines,andparticulates withhalflivesgreaterthaneightdays,thecriticalpathwaysaregrass-(cow andgoat)-milk, grass-cow meat,vegetation, inhalation anddirectradiation (groundplane)asaresultofgrounddeposition.

Thegrass-(cow andgoat)-milk, andgrass-cow-meat pathwayswillbebasedonthegreatest0/Qlocation.

Thislocationhasbeendetermined incon]unction withthelandusecensus(technical specification 3.6.22)andissub]ecttochange.Thevegetation (foodcrop)pathwayisbasedonthegreatest0/Qgardenlocationfromwhich,samplesaretaken.Thislocationmayalsobemodifiedasaresultof-vegetation samplingsurveys.39

$*PC4gi+1 3.3(Cont'd)TocomplywithTechnical Specifications, theinhalation andground'lanedosepathwayswill.be.,calculated atthesiteboundaryandbeyondatthecriticalresidence.

BecausetheTechnical Specifications statetocalculate "atthesiteboundaryandbeyond",insteadof"atthesiteboundaryorbeyond",suchasUnit2,thedosesand/ordoseratesmustbecalculated foramaximumindividual whoisexposedtoallpathwaysatthesiteboundaryandatthecriticalresidence.

Themaximumindividual isacomposite ofthehighestdosefactorofeachagegroup,foreach'rganandtotalbody,andeachnuclide.Sincethecriticalresidence locationwouldhavethegreatestoccupancy time,theresultant doseattheresidence including allpathwaysislimiting.

However,duetothetechnical specif1cation wording,theinhalat1on andgroundplanedoseatthesiteboundaryalongwithallotherpathway's, willbecalculated assumingacontinuous occupancy time.tIn11euofcorrecting thelandsiteboundarygroundplaneandinhalation dosefactorsforoccupancy t1me,aTechnical Specif1cation changewillbesubmitted tochangetherequirement fromcalculating "atthesiteboundaryandbeyond"to"atthesiteboundaryorbeyond".Unitlwillthencalculate atthecritical'res1dence sincethisshouldbethe11mit1ngdose.Untilthischangeiseffective, thedoseand/ordoseratecalculations fortrit1um,iodines,andparticulates withhalflivesgreaterthan8dayswillconservatively assumethatthegroundplaneandinhalation pathwaycr1ticalreceptors areatthesiteboundary, i.e.X/Qand0/Q,respectively,

~arecalculated atthes1teboundary.

40 VfIVIC'*

3,4Refinement ofOffsiteDosesResulting fromEmergency Condenser VentReleases.

Thedosesresulting from.theoperation oftheemergency condensers andcalculated inaccordance with3.2.2mayberefinedusingdatafromactualenvironmental samples.Grounddeposition sampleswillbeobtainedfromanareaorareasofmaximumprojected deposition.

Theseareasareanticipated tobeatornearthesiteboundaryand.nearprojected plumecenterline.

Usingthemethodology foundinRegulatory Guide1.109,thedosewillbecalculated tothemaximumexposedindividual.

Thisdosewillthenbecomparedtothedosecalculated inaccordance with3.2.2.Thecomparison wi11resultin"anadjustment factoroflessthanorgreaterthanonewhichwillbeusedtoadjusttheotherdosesfromotherpathways.

Otherenvironmental samplesmayalsobecollected andtheresultant calculated dosestothemaximumexposedindividual comparedtothedosecalculated per3.2.2.,Otherenvironmental samplemediamay.includemilk,vegetation (suchasgardenbroadleaf vegetables),

etc.Theadjustment factorsfromthesepathwaysmaybeappliedtothedosescalculated per3.2.2onapathwaybypathwaybasisorseveralpathwayadjustment factorsmaybeaveragedandusedtoadjustcalculated doses.Dosescalculated'from actualenvironmental samplemediawillbebasedonthemethodology presented inRegulatory Guide1.109.Theregulatory guideequations maybeslightlymodifiedtoaccountforshortintervals oftime(lessthanoneyear)ormodifiedforsimplicity purposesbydeletingdecayfactors.Deletionofdecayfactorswoul'dyieldmoreconservative results.

c~1*III

4.0 40CFR190REQUIREMENTS

The"UraniumFuelCycle"isdefinedin40CFRPart190.02(b)asfollows:"Uraniumfuelcyclemeanstheoperations ofmillingofuraniumore,chemicalconversion ofuranium,isotopicenrichment ofuranium,fabrication ofuraniumfuel,generation ofelectricity byalight-water-cooled nuclearpowerplantusinguraniumfuel,andreprocessing ofspenturaniumfuel,totheextentthatthesedirectlysupporttheproduction ofelectrical powerforpublicuseutilizing nuclearenergy,butexcludesminingoperations, operations atwastePdisposalsites,transportation ofanyradioactive materialinsupportoftheseoperations, andthereuseofrecovered non-uranium specialnuclearandby-product materials fromthecycle."Section3.6.15.doftheTechnical Specifications requiresthatwhenthecalculated dosesassociated withtheeffluentreleasesexceedtwicethelimitsofsections3.6.15.a.(2)(b),

3.6.15.b.(2)(b) and3.6.15.b.(3)(b),

thencalculations shallbemadeincluding directradiation contributions fromthereactorunitsandoutsidestoragetanks(asapplicable) todetermine whetherthe40CFR190doselimitshavebeenexceeded.

$1%

4.0(Cont'd)Ifsuchisthecase,NiagaraMohawkshallsubmitaSpecialReporttoth'e'NRCandlimit"subsequent releasessuchthatthedosecommitment toarealindividual fromalluraniumfuelcyclesourcesislimitedto<25mremtothetotalbodyoranyorgan(exceptthethyroid,whichislimitedto<75mrem)overthecalendaryear.Thisreport=istodemonstrate that.radiation exposures toallrealindividuals fromalluraniumfuelcyclesources(including allliquidandgaseouseffluentpathwaysanddirectradiation) arelessthanthelimitsin40CFRPart190.Ifreleasesthatresultindosesexceeding the40CFR190limitshaveoccurred, thenavariancefromtheNRCtopermitsuchreleaseswillberequested andifpossible, actionwillbetakentoreducesubsequent releases.

ThereporttotheNRCshallcontain:1)'dentification of,alluraniumfuelcyclefacilities oroperations within5milesofthenuclearpowerreactorunitsat.thesitethatcontribute totheannualdoseofthemaximumexposedmemberofthepublic.2)Identification ofthemaximumexposedmemberof-thepublicandadetermination ofthetotalannualdosetothispersonfromexistingpathwaysandsourcesofradioactive effluents anddirectradiation.

~-

4.p(Cont'd)Themaximumtotalbodyandorgandosesresulting fromradioactive materialinliquideffluents"from NineHilePointUnit1willbesummedwiththemaximumdosesresulting fromthereleasesofnoblegases,radioiodines, andparticulates fortheothercalendarquarters(asapplicable) andfromthecalendarquarterinwhichtwicethe'imitwasexceeded.

Thedirectdosecomponents willbe-determined byeithercalculation oractualmeasurement.

Actualmeasurements willutilizeenvironmental TLOdosimetry.

Calculated measurements willUtilizeengineering calculations todetermine aprojected directdosecomponent.

Intheeventcalculations areused,themethodology will"bedetailedasrequiredinSection6.9.3.eoftheTechnical Specifications.

ThedosesfromNineHilePointUnit1willbeaddedtothedosestothemaximumexposedindividual thatarecontributed fromotheruraniumfuelcycleoperations within5milesofthesite.Forthepurposeofcalculating doses,theresultsoftheRadiological Enviromental Honitoring Programmaybeincludedforproviding morerefinedestimates ofdosestoarealmaximumexposedindividual.

Estimated doses,ascalculated fromstationeffluents, maybereplacedbydosescalculated fromactualenviromental sampleresults..

44 p~if1E)It\I,*%lPCq Evaluation ofOosesFromLiquidEffluents Fortheevaluation ofdosestorealmembersofthepublicfromliquideffluents, thefi'shconsumption andshoreline sedimentgrounddosewillbeconsidered.

Sincethedosesfromotheraquaticpathwaysareinsignificant, fishconsumption andshoreline sedimentaretheonlytwopathways'thatwillbeconsidered.

Thedoseassociated withfishconsumption maybecalculated usingeffluentdataandRegulatory

~Guide1.109methodology orbycalculating adosetomanbasedonactualfishsampleanalysisdata.Thedoseassociated withshoreline sedimentisbasedontheassumption thattheshoreline wouldbeutilizedasarecreational area.ThisdosemaybederivedfromliquideffluentdataandRegulatory Guide1.109methodology orfromactualshoreline sedimentsampleanalysisdata.Equations usedtoevaluatedosesfromactualfishandshoreline sedimentsamplesarebasedonRegulatory Guide1.109methodology.

Becauseofthesamplemediumtypeandthehalf-lives oftheradionuclides historically

observed, thedecaycorrected portionsof'---the-equations are.deleted.,

Thisdoesnotreducetheconservatism ofthecalculated dosesbutincreases thesimplicity fromanevaluation pointofview.Thedosefromfishsamplemediaiscalculated as:(1)Rwb~Zi[CifxUx1000xOiwbxflNhere:RwbThetotaldosetothewholebodyofanadultinmremperyear.

l8k.1lr"Uiig-f4"4%9,vvtf,VS (Cont'd)Cif1000Diwb(2)RlWhere:Theconcentration ofradionuclide iinfishsamplesinpCi/gram.

Theconsumption rateoffishforanadult(21kgperyear).Gramsperkilogram-Thedosefactorforradionuclide iforthewholebodyofanadult(R.G.1.109,TableE-11).IThefractional portionoftheyearoverwhichthedoseisapplicable.

gi(CifxUx1000xDilxf]RlThetotaldosetotheliverofanadult(maximumexposedorgan)inmremperyear.CifTheconcentration ofradionuclide iinfishsamplesinpCi/gram.

Theconsumption rateoffishforanadult(21kgperyear).1000DilThedoseRwbRskWhere:GramsperkilogramThedosefactorforradionuclide.

tfortheliverofanadult(R.G.1.109,TableE-11)-Thefractional portionoftheyearoverwhichthedoseis.applicable.

fromshoreline sedimentsamplemediaiscalculated as:I~X[iCisxUx40,000x0.3xDiwbxf]andXhiCisxUx40,000x0.3xDiskxf]RwbRskCisThe.totaldoseto.thewholebodyofateenageror.adult(maximumexposedagegroup)inmremperyear.Thetotal:dosetotheskinofa.teenager oradult(maximumexposedagegroup)inmremperyear.Theconcentration ofradionuclide iinshoreline sedimentinpCi/gram.

Ci'Lk (Cont'd)Theusagefactor.Thisisassumedas67hoursperyearbyateenageroradult.40,000Theproductoftheassumeddensityofshoreline sediment(40kilogrampersquaremetertoadepthof2.5cm)times'thenumberofgramsperkilogram.

0.3Theshorewidthfactorforalake.Diwb0is-The'osefactorforradionuclide iforthewholebody(R.G.1.109,TableE-6)-Thedose'actor forradionuclide ifortheskin(R.G.1.109,TableE-6)='The-fractional portionoftheyearoverwhichthedoseisapplicable.

NOTE:Becauseofthenatureofthereceptorlocationandtheextensive fishingactivityinthearea,thecriticalindividual maybeateenageroranadult.47 Qflvp~4'4.lP 4.2Evaluation ofDosesFromGaseousEffluents Fortheevaluation ofdosestorealmembersofthepublicfromgaseouseffluents, thepathwayscontained insection3.2.2.3oftheODCMwillbeconsidered.

Theseincludethedeposition, inhalation andingestion pathways.

However,anyupdatedfielddatamaybeutilizedthatconcernslocations ofrealindividuals, realtimemeteorological data;locationofcriticalreceptors,

-etc..Data.from'hemost-recentcensusandsamplelocationsurveysshouldbeutilized.

Dosesmayalsobecalculated fromactualenviromental samplemedia,asavailable.

Enviromental samplemediadatasuchasTLO,airsample,milksampleandvegetable (foodcrop)sampledatamaybeutilizedinlieuofeffluentcalculational data.Dosestomemberofthepublicfromthepathwayscontained inOOCMsection3.2.2.3as.aresultofgaseouseffluents willbecalculated

'singthedosefactorsofRegulatory Guide1.109orthemethodology oftheODCM,asapplicable

.Dosescalculated fromenvironmental samplemediawillutilizethemethodologies foundinRegulatory Guide:,1.109.4.3Evaluation ofDosesFromDirectRadiation Section3.6.15.dofthe'echnical-Specificationsrequires thatthe.dosecontribution asaresultofdirectradiation be.considered whenevaluating whetherthedoselimitations of40CFR190havebeen.exceeded.

CgIPI'1L4A Directradiation dosesasaresultofthereactor,turbineandradwastebuildings andoutsideradioactive storagetanks(asapplicable) maybeevaluated byengineering calculations orbyevaluating enviromental

'TLDresultsatcriticalreceptorlocations, siteboundaryorotherspecialinterestlocations.

Fortheevaluation ofdirectradiation dosesutilizing environmental TLDs,thecriticalreceptorinquestion, suchasthecriticalresidence, etc.,wi11be'ompared to.thecontrollocations.

Thecomparison

-involves thedifference'in environmental TLDresultsbetweenthereceptorlocationandtheaveragecontrollocationresult.4,4DosestoMembersofthePublicWithintheSiteBoundary.

Section6.9.l.eoftheNineMilePointUnit1Technical Specifications requiresthattheSemiannual Radioactive Effluent'ReleaseReportincludeanassessment oftheradiation dosesfromradioactive liquidandgaseouseffluents tomembersofthepubli'cduetotheiractivi,ties insidethesiteboundaryasdefinedbyFigure5.1-1ofthespecifications.

Amemberofthepublic,asdefinedby--=theTechnical Specifications, wouldberepresented byanindividual whovisitsthesites'nergy Information Centerforthepurposeofobserving theeducational displaysorforpicnicing andassociated activities..

49 1'4g' 4.4(Cont'd)Fishingisamajorrecreational activityintheareaandontheSiteasaresultofthesalmonidandtroutpopulations inLakeOntario.Fishermen havebeenobservedfishingattheshoreline neartheEnergyInformation CenterfromAprilthroughOecemberinallweatherconditions

.Thus,fishingisthemajoractivityperformed bymembersofthepublicwithinthesiteboundary.

Basedonthenatureofthe-.fishermen.

and.undocumented observations, itisconservatively assumedthatthemaximumexposedindividual spendsanaverageof8hoursperweekfishingfromtheshoreline atalocationbetweentheEnergyInformation CenterandtheUnit1facility.

Thisestimateisconsidered conservative butnotnecessarily excessive andaccountsforoccasions whereindividuals mayfishmoreonweekendsoronafewdaysinMarchoftheyear.Thepathwaysconsidered fortheevaluation includetheinhalation pathwaywiththeresultant lungdose,thegrounddosepathwaywiththeresultant wholebodyandskindoseandthedirectradiation dose;,pathwaywiththeassociated wholebodydose.Thedirectradiation dosepathway,inactuality, includesseveralpathways.

Theseinclude:thedirectradiation gammadosetoanindividual fromanoverheadplume,agammasubmersion plumedose,possibledirectradiation dosefromthefacilityandagroundplanedose(deposition).

Becausethelocationisincloseproximity tothesite,anybetaplumesubmersion doseisfelttobeinsignificant.

WS4I16UIIIfIp 4.4(Cont'd)Otherpathways, suchastheingestion pathway,arenotapplicable.

Inaddition, pathwaysassociated withwaterrelatedrecreational activities, otherthanfishing,arenotapplicable here.Theseincludeswimming, boatingandwadingwhichareprohibited atthefacility.

-The1nhalation pathwayisevaluated byidentifying theapplicable radionuclides (radioiodine, tritiumandparticulates) intheeffluentfortheappropriate t1meper1od.Theradionuclide concentrations are~:thenmultiplied bytheappropriate X/Qvalue,1nhalatton dosefactor,airintakerate,andthe.fractional portionoftheyearinquestion.

Thus,theinhalation pathwayisevaluated usingthefollowing equationadaptedfromRegulatory Guide1.109.NOTE:Thefollowing equation1sadaptedfromequations C-3andC-4ofRegulatory Guide1.109.SincemanyofthefactorsareinunitsofpCi/m,m/sec.,etc.,andsincethe33.-radionuclide decay.expressions havebeendeletedbecauseoftheshortdistancetothereceptorlocation, theequationpresented hereisnotident1cal totheRegulatory Guide..equations.

R~gi['CiFX/QDFA1)Rt]where:R'themaximumdosefortheperiodinquestiontothelung(])forallradionuclides (1)fortheadultagegroup(a)inmrempertimeperiod.

lt"r$C1ww,CA'f~ITkPk 4.4(Cont'd)X/QTheaverageconcentration inthestackreleaseofradionuclide 1inpCi/m3fortheperiodinquestion.

Unitlaveragestackflowrateinm3/sec.The.plume;dispersion parameter foralocationapproximately 0.50mileswestofNHP-1(Theplumedispersion parameter is8.9E-06andwasobtainedfromtheC.T.HainfiveyearaverageannualX/Qtables.Thestack(elevated)

X/Qisconservat1ve whenbasedon0.50milesbecauseofthecloseproximity ofthestackandthereceptorlocation).

OFAiga.theinhalation dosefactorforradionuclide 1,thelung],andadultagegroupainmremperpCifoundon6TableE-7ofRegulatory Guide1.109.Raannualairintakeforindividuals inagegroupainm3peryear(thisvalueis8,000m3peryearandwasobtainedfromTableE-5ofRegulatory Guide1.109).fractional portionoftheyearf'rwhichradionuclide 1wasdetectedandforwhichadoseistobecalculated (inyears).Thegrounddosepathway(deposition) willbeevaluated byobtaining atleastonesoilorshoreline sedimentsampleintheareawhere"fishingoccurs.Thedosewillthenbecalculated us1ngthesampleresults,thetimeperiodinquestion, andthemethodology basedonRegulatory Guide1;109aspresented inSection4.1.Theresultant dosemaybead)ustedforabackground dosebysubtracting the"'applicable off-sitecontrolsoilorshorel1ne sedimentsamplerad1onuclide activities.

Intheeventitisnotedthatfishingisnotperformed fromtheshoreline, butisinsteadperformed inthe'water(i.e.,theuseofwaders),thenthegrounddosepathway.(depos1t1on) willnotbeevaluated.

52 1<<llI~'*A Thedirectradiation gammadosepathwayincludesanygammadosesfromanoverheadplume,submersion intheplume,possibleradiation fromthefacilityandgroundplanedose(deposition).

Thisgeneralpathwaywillbeevaluated'y averageenvironmental TLDreadings.

Atleasttwoenvironmental TLDswillbeutilizedatonelocationintheapproximate areawherefishingoccurs.TheTLOswillbeplacedinthefieldonapproximately"the beginning ofeachcalendar.'quarter-.and removedonapproximately theend-ofeachcalendarquarter(quarter2,3,and4).TheaverageTLDreadingswillbead]ustedbytheaveragecontrolTLDreadings.

Thisisaccomplished bysubtracting theaveragequarterly controlTLDvaluefromtheaveragefishinglocationTLOvalue.Theapplicable quarterly controlTLDvalueswillbeutilizedafterad]usting fortheappropriate timeperiod(asapplicable).

IntheeventoflossortheftoftheTLDs,resultsfromaTLDorTLOsintheareamaybeutilized.

EV1Pt4pl+{I%')ll~1

5.0 ENVIRONMENTAL

MONITORING PROGRAM5.1SamplingStationsThecurrentsamplinglocations arespecified inTable5-1andFigures5.1-1,5.1-2.Themeterological towerisshowninFigure5.1-1.ThelocationisshownasTLDlocation17.TheRadiological Environmental Monitoring Programisa'jointeffortbetweentheNiagaraMohawkPower,Corporation andtheNewYorkPowerAuthority, theownersandoperators oftheNineMilePointUnit1andtheJamesA.FitzPatrick NuclearPowerPlant,respectively.

Samplinglocations arechosenonthebasisofhisto'rical averagedispersion ordeposition parameters frombothunits.Theenvironmental samplinglocationcoordinates shownonTable5-1arebasedontheNMP-2reactorcenterline.

Theaveragedispersion anddeposition parameters havebeencalculated fora5yearperiod,1978through1982.Thesedispersion calculations areattachedasAppendixE.""""'->The calculated, dispersion or.deposition parameters willbecomparedtotheresultsoftheannuallandusecensus.If.itisdetermined thatamilksamplinglocationexistsatalocationthatyieldsasignificantly higher(e.g.50'4)calculated 0/Qrate,thenewmilksamplinglocationwillbe-addedtothemonitoring programwithin30days.Ifanewlocationisadded,theoldlocationthatyieldsthelowestcalculated D/QmaybedroppedfromtheprogramafterOctober31ofthatyear.

g..~'t 5.2Interlaboratory Comparison ProgramAnalysesshallbeperformed onsamplescontaining knownquantities ofradioactive materials thataresuppliedaspartofaCommission approvedorsponsored Interlaboratory Comparison Program,suchastheEPACrosscheck Program.Participation shallbeonlyforthosemedia,e.g.,air,milk,water,'tc.,

thatareincludedintheNineNilePointEnvironmental Monitoring-Program andforwhichcrosscheck

"=samples areavailable.

'AnattemptwillbemadetoobtainaQCsampletoprogramsampleratioof5'Lorbetter.Thesiteidentification symbolortheactualgualityControlsampleresultsshallbereported~intheAnnualRadiological Environmental Operating Reportsothatthe'ommission staffmayevaluatetheresults.aSpecificsamplemediaforwhichEPACrossCheckProgramsamplesare..available includethefollowing:

,0grossbetainairparticulate filters',gammaemittersinairparticulate filtersgammaemittersinmilk,gammaemittersinwatertritiuminwaterI-131inwater lJPPl~V~K'KII0 5.3Capabilities forThermoluninescent Dosimeters UsedforEnv/ronmental Measurements Requireddetection capabilities forthermoluminescent dosimeters usedforenvironmental measurements requiredbyTable4.6.20-1, footnoteboftheTechnical Specifications arebasedonANSIStandardN545,section4.3.TLOsaredefinedasphosphors packagedforfielduse.Inregardtothe"detection capabilities forthermoluminescent dosimeters, only,onedetermination isrequiredtoevaluatetheabovecapabilities pertypeofTLD.Furthermore, theabovecapabilities maybedetermined bythevendorwhosuppliestheTLDs.Requireddetection capabilities areasfollows:5.3.1Uniformity shallbedetermined bygivingTLOsfromthesamebatchanexposureequaltothatresulting fromanexposurerateof10uR/hrduringthefieldcycle.Theresponses obtainedshallhavearelativestandarddeviation oflessthan7.5'A.Atotalofatleast5TLOsshallbeevaluated.

--;5.3.2-~'-",Reproducibility shall-.be determined.

bygivingTLDsrepeatedexposures equal.tothatresulting fromanexposurerateof10uR/hrduringthefieldcycle.Theaverageoftherelativestandarddeviations ofthe,.responses.

shallbelessthan3.0'X.Atotalofatleast4TLOsshallbeevaluated.

'11p,,Alj1!-CfWf 5.3.3Dependence ofexposureinterpretation onthelengthofafieldcycleshallbeexaminedbyplacingTLDsforaperiodequaltoatleastafieldcycleandaperiodequaltohalfthesamefieldcycleinanareawheretheexposurerateisknowntobeconstant.

Thistestshallbeconducted underapproximate averagewintertemperatures andapproximate averagesummertemperatures.

Forthesetests,theratiooftheresponseobtainedinthefieldcycletotwicethatobtainedforhalfthefieldcycleshallnotbelessthan0.85.Atleast6TLDsshallbeevaluated 5.3.4Energydependence shallbeevaluated bytheresponseofTLDstophotonsforseveralenergiesbetweenapproximately 30keVand3HeV.Theresponseshallnotdifferfromthatobtainedwiththecalibration sourcebymorethan25%forphotonswithenergiesgreaterthan80keVandshallnotbeenhancedbymorethanafactoroftwoforphotonswithenergieslessthan80keV.Atotalofatleast8TLDsshallbeevaluated.

5.3.5Thedirectional dependence oftheTLDresponseshallbedetermined by'omparing

.theresponseoftheTLDexposedintheroutineorientation withrespecttothecalibration sourcewiththeresponseobtainedfordifferent orientations.

Toaccomplish this,theTLDshallberotatedthroughatleasttwoperpendicular planes.Theresponseaveragedoveralldirections shallnotdifferfromtheresponseobtainedin.thestandardcalibration positionbymorethan10K.Atotalofatleast4TLDsshallbeevaluated.

V~(I~lgsS 5.3.6Lightdependence shallbedetermined byplacingTLDsinthefieldforaperiodequaltothefieldcycleunderthefourconditions foundinANSIN545,section4.3.6.Theresultsobtainedfortheunwrapped TLOsshallnotdifferfromthoseobtainedfortheTLDswrappedinaluminumfoilbymorethan10K.Atotalofatleast4TLOsshallbeevaluated foreachofthefourconditions.

5.3.7Moisturedependence shallbe..determined byplacingTLDs(thatls,thephosphors packagedforfielduse)foraperiodequaltothefieldcycleinanareawheretheexposurerateisknowntobeconstant.

TheTLDsshallbeexposedundertwoconditions:

(1)packagedinathin,sealedplasticbag,and(2)packagedinathin,sealedplasticbagwithsufficient watertoyieldobservable moisturethroughout thefieldcycle.TheTLDorphosphor, asappropriate, shallbedriedbeforereadout.TheresponseoftheTLDexposedintheplasticbagcontaining watershallnotdifferfromthatexposedintheregularplasticbagbymorethan10'L.Atotalofatleast4TLOsshallbeevaluated foreachcondition.

.,'.3.8.=,Selfirradiation shall-bedetermined.

byplacingTLOsforaperiodequaltothefieldcycleinanareawheretheexposurerateislessthan10uR/hrandtheexposureduringthefieldcycleisknown.Ifnecessary,.

corrections shallbeappliedforthedependence ofexposureinterpretation on.thelengthofthefieldcycle(ANSIN545,section4.3.3).Theaverageexposureinferredfromtheresponses oftheTLDsshallnotdifferfromtheknownexposurebymorethananexposureequaltothatresulting fromanexposurerateof10uR/hrduringthefieldcycle.Atotalofatleast3TLDsshallbeevaluated.

I~'+III~llltd~~l&III&RIfl"l.I+II~l~PII+5"IIllIIIIfI'rC TABLE1-1AverageEnergyPerDisintegration ISOTOPEAr-41Kr-83mKr-85Kr-85mKr-87Kr-88Kr-89Kr-90Xe-'131MXe-133Xe-133mXe-135Xe-135mXe-137Xe-138~Emev/dis1.2940.002480.00220.1590.7931.952.222.10'0.02010.04540.0420.2470.4320.1941.18(Ref)(3)(2)(2)EGmev/dis<4) 0.4640.03710.2500.2531.320.3771.371.010.1430~1350.190.3170.0951.640.611(Ref)(3)(2)(2)(1)ORNL-4923, Radioactive Atoms-SulementI,M.S.Martin,November1973.(2)NED0-12037, "SummaryofGammaandBetaEmittersandIntensity Data";M.E.Meek,R.S.Gilbert,January1970.<TheaverageenergywascomputedfromthemaximumenergyusingtheICRPIIequation, notthe1/3value.:assumption used,inthisreference).

(3)NCRPReportNo.58,-,"A-Handbook of.Radioactivity Measurements Procedures";

1978(4)Theaverageenergyincludesconversion electrons.

59 Q,VkC$,ag2spI4I't'4\A4A\pgyA~lb~la-,IS&

NUCLIDEBONELIVERH3-2.90E-1Cr51TABLE2-1AitVALUES-LIQUID*RADHASTETANKINFANT,mrem-mlhr-uCiTBODYTHYROIDKIDNfY2.90E-12.90E-12.90E-11.29E-28.39E-31.83E-3LUNGGI-TRACT2.90f-l2.90E-11.63E-23.75E-1Cu64Mn541.13E-l1.87E+15.23E-21.91E-l4.23-4.142.326.864.131.071.47E+12.37E+18.332.42E+15.00E+14.77E+1~-2.17E+22.32E+12.18E-2.7.712.372.371.281.041.15E-22.60E-42.26FE551.31E+18.441.96E+1Fe592.84E+14.96E+18.342.40E+1Co58-3.34Co60-1.02f+1Zn651.72f+15.91E+1Sr89*2.32E+32.73E+1-2.87E+16.66E+14.43E+3Sr901.74E+4Zr951.91E-l4.66E-25.02E-22.07E-43.30E-2'.15E-5 2.40E-4Mn563.50E+12.374.17E+12.34E+14.57Mo99Na24I131I1332.37'2.372.371.57E+12.373.54E+16.151.17E+43.03E+14.221.801.12E+37.231.33E-31.51E-46.85E-5Ni65I132's'1341.58E-43.21E-41.14E-41.50E-23.58E-43.54E+2-.6.60E+24.05f+11.19f+26.67E+14.45E+11.70E+26.97E+11.794.75E+19.71E+11.811.54E+26.24E+11.803.57E-29.23E-23.69E+1Cs136Cs137Ba140Ce141Nb954.91E+25.75E+24.07E+11.50E+21.SOE-17.747.21E-2'.

4.40E-25.17E-33.85E-21.59E-29.18E-32.27E+11.34E+15.48E+11.60E+21.36E-21.14E-21;andRegulatory La1401.18E-24.67E-31~20E-3Ce1442.791.141.57E-1-4.62E-l*Calculated inaccordance withNUREG0133,Section4.3.Guide1.109,Regulatory positionC,Section1.60 kVt~.VQQI'p9g'0%(V>>sQ/

TABLE2-2AitVALUES-LIQUID*RADHASTETANKCHILDmrem-mlhr-uCiLIVERTBODYTHYROID.KIDNEY4.39E-14.39E-l4.39E-14.39E-1NUCLIDEBONEH3Cr512.13E-2CU642.51E-6Mn546.92Fe559.21E+2Fe591.30E+3Co581.89Co601.12E+2Zn652.15E+4'r89'"3.'26E+4Sr904.26f+5Zr951.70Mn56Mo995.35E-3Na241.52E+2I1312.09E+2I1333.39E+1Ni652.67E-lI1326.13E-3='Cs134~;3.68E+5Cs1363.52E+4Cs1375.15E+5Ba1403.61E+2Ce.1411.50f-lNb955.21E+2La1401.50E-lCe1445.00Calculated inGuide1.109,ReguLUNG4.39E-1GI-TRACT4.39E-l7'1E+12.13E-21.407.86E-12.30E-11.422.51E-61.27E+22.701.632.51E-66.529.53E+23.38E+39.06E+26.924.88E+21.51E+22.11E+31.05E+31.347.46E+12.24E+21.896.92.2.84E+32.76E+29.05E+12.19E+34.26E+26.12E+21.341.&91.893.28E+27.4&E+21.12E+21.12E+21.,12E+21.31E+33.61E+41;10E-45.73E+43.56E+43.85'1.10E-49.32E+21.10E-41.0&f+51.01E+43.851.10E-41.26E+35.74E+31.231.08E+22.39E+11.331.321.381.232.00E-11.65E-l3.73E-27.91E+11.52E+29.57E+12.37E+15.35E-32.04E+25.35E-3'1.52E+21.52E+21.52E+21.52E+21.52E+22.10E+21.19E+26.94E+43.45E+25.60E-21.87E+14.19E+11.59E+17.7&E+32.51E-21.47E-26.98E+11.38f-41.69E+13.081.32E-21.13E-25.18E-35.22E-11.72E-29.67E+46.26E+46.21E-14.93E+57.28E+45.37E+13.96E-12.11E+17'6E-2:1.07E-16.99E-Z6.34E-Z2.03E+21.45f+26.39E-l5.93E-22.6&E-21.03E-21.816.06f-l3.58E-1accordance withNUREG0133,Slatoryposi'tion C,Sectionl.5.15E+47.68E+33.40f+31.61E+55.78E+43.14E+31.82E-18.24E-21.91E+21.03E-22.68E-l1.83E+26.34E-2.5.40E+16.39E-13.75E+51.03E-21.36E+33.58E-l3.80E+21;andRegulatory 1.16ection4.3.;,6.04E+5 1..27E+53.54E+11.87E+56.72E+43.29E+361 b~4 TABLE2-3AitVALUES-LIQUID*RADHASTETANKTEENmrem-mlKIDNEYLUNGGI-TRACT3.28E-13.28E-13.28E-11.20E-S2.24E+27.89E+25.87E+31.24E+33.93E+39.034.66E+41.84E+13.08E+45.24E-45.24E-42.90E+31.31E+45.902.28E+21.19E+12.29E-l2.11E+22.56E-21.65E+21.39E+21.39E+21.39E+22.68E-l4.30E+16.60E-43.25E+11.445.59E-38.73E+49.10E+31.01E+49.44E+37.21E+47.99E+35.75E-l3.63E+23.04E-1.8.16E+13.061.05E+64.94E-23.05E+31.715.74E+2;andRegulatory hr-uCiNUCLIDEBONELIVERTBODYTHYROIDH3-3.28E-13.28E-13.28E-1Cr511.02E-l1.02E-l1.39.8.16E-l3.84E-l1:942.1'6E+2Cu641.20E-S2.891.361.20E-57.32Hn54-3.3lf+14.34E+38.87E+23.31E+11.32E+33.'31E+18.86E+3Fe,55-;6.94E+24.92E+21.15E+2--3.12E+22.13E+2fe591.07E+32.49E+39.64E+26.416.41Co589.039.82E+12.15E+29.039.03Co605.36E+27.96E+21.12E+35.36E+25.36E+25.36E+2Zn652.10E+47.28E+4,3.40E+41.84E+1'r89"2.44E+4'.24E-46.98E+25.24E-4,Sr904.66E+51.15E+5Zr956.206.005.975.906.04Hn56-1.81E-13.22E-2Ho992.56E-29.22E+11.76E+12.56E-2'Na241.39E+2'1':39E+2 1.39E+21.39E+2I1311.55E+22.17E+21.16E+26.31E+43.73E+2I1332.53E+14.29E+11.31E+15.99E+37.52E+1Ni652.08E-l2.66E-21.21E-2I1324.90E-21.28E-24.60E-34.32E-12.02E-2'Cs'34'3.05f+5'7.18E+5"3.33E+51.69E+22.28E+5Cs1362.98E+41.17E+57.88E+42.976.38E+4Cs1374.09E+55.44E+51.90E+52.57E+21.85E+5Ba1402.35E+24.10E-l1.55E+13.81E-l4.79E-1Ce.1413.46E-1'-3.32E-l3.07E-1,3.04E-13.17E-lNb954.44E+2.2.48E+2.1..18E+2 3.062.40E+2La1401.57f-l1.02E-l6.35E-2'.94E-2'.94E-2Ce1443.992.651.831.712.27*Calculated inaccordance withNUREG0133,Section4.3.1Guide1.109,Regulatory positionC,Section1.62

~4Vf,)EnJsl$k-Pi'w TABLE2-4AitVALUES-LIQUID*RADWASTETANKADULTmrem-mlhr-uCiGI-TRACTLUNGKIDNEY4.45E-l2.93E-1TBODYTHYROIDNUCLIDEBONELIVER4.45E-l4.45E-1H3Cr51CU644.45E-14.45E-14.45E-11.277.64E-11.82E-23.14E+22.35E+21.34E+42.63E+21-82E-21.676.942.751.291.31E+35.94Mn545.944.38E+38.41E+25.942.56E+26.79E+21.629.60E+11.07E+24.58E+26.64E+21.03E+3Fe55Fe598.09E+31.82E+31~151.159.31E+22.43E+31.621.622.03E+29.15E+1Co581.62Co609.60E+14.99E+34.63E+43.60E+31.62E+49.60E+19.60E+16.71E+22.57E+24.92E+43.303.30Zn65Sr89SI90Zr95Mn56Mo99Na24I131I133Ni65I1322.31E42.25E+45.60E+51.364.58E-3'.35E+21.45E+22.35E+11.93E-l4.68E-37.36E+43.32E+49.39E-56.45E+29.39E-59.39E-S9.39E-51.37E+51.15E1.121.061.213.06E+25.522.02E+21.35E+21.061.73E-13.07E-22.20E-18.70E+11.97E+24-58E-31.66E+14.58E-31.35E+'21.35E+21.35f+21.35E+21.35E+22.51E-21.14E-26.36E-12.35E-31.24E+41.33E+41.25E-24.38E-34.38E-l2.00E-27.61E+48.93E+3Cs"134Cs136Cs137Ba140Ce..141Nb95La140Ce144.5.79f+58.42E+4'7".OBE+5 1.17E+55.22E+53.49E-l-2:98E+52.96E+43.82E+52.24E+29.53E-24.39E+2l.llf-l2.482.29E+56.51E+43.03E+15.32E-14.60E+16.83E-21.02E+41.77f+55.90E+43.42E+51.47E+14.61E+21.64E-12.29E-18.20E-25.75E-25.44E-21.06E+21.48E+66.72E-25.44E-22.41E+25'7E-12.44f+21.32E+25.47E-1,6.03E-22.24E-28.84E-31.224.24E-13.07E-1accordance withNUREG0133,SlatorypositionC,Section1.8.84E-38.84E-33..78E+38.47E-l3.07E-l7.37E+2ection4.3.1;andRegulatory Calculated inGuide1.109,Regu2.07E+21.19E+26.79E+43.55E+24.80E-25.47E+14.09E+11.25E+16.02E+37.14E+11.18E-43.68E+163

~a0 NUCLIDEBONELIVERH3-7.43E-4TABLE2-5AitVALUES-LIQUID*EHERGENCY CONDENSER VENTINFANTmrem-mlhr-uCiTBODYTHYROIDKIDNEYLUNGGI-TRACT7.43E-47.43E-47.43E-47.43E-47.43E-4Cr51Cu64Hn542.89E-41.34E-44.89E-45.94E-34.79E-21.'08E-21.06E-21.76E-23.30E-52.15E-54.70E-64.18E-59.61E-4,Fe55,3.35E-22.16E-25.78E-3Fe597.29E-21.27E-15.02E-21.06E-22.75E-33.76E-26.08E-22.14E-26.19E-21.28E-l1.22E-15.57E-l5.95E-25.60E-51.98E-2Co58Co608.58E-32.14E-22.60E-26.15E-27.35E-2Zn654.42E-21.52E-16.99E-2Sr895.95Sr904.46E+11.71E-l1.14E+11.19E-4Zr954.90E-4Hn56Ho99Na24.6.07E-3I1317.77E-ZI1331.08E-2Ni653.41E-6I1324.05E-7'Cs'134'.'OBE-1Cs1361.04E-1Cs1371.26Ba1403.85E-lCe1411.85E-4Nb959.88E-5La1403.03E-5Ce1447.16E-3*Calculated inGuide1.109,Regu8.47E-51.29E-45.30E-78.97E-26.17E-71.06E-71.17E-26.00E-26.07E-36.07E-36.07E-36.07E-36.07E-36.07E-33.27E-32.67E-32.94E-56.66E-79.16E-23.01E+11.07E-12.871.85E-24.03E-21.58E-24.62E-31.76E-73.86E-78.22E-72.93E-73.85E-59.17E-73.06E-11.14E-l1.22E-12.49E-24.64E-31.471.04E-1-3.95E-I1.60E-14.61E-31.99E-23.85E-49.15E-52.37E-49.47E-25.82E-21.13E-41.33E-53.48E-52.92E-54.07E-52.35E-5--3.43E-21.41E-l4.11E-lRegulatory 3.08E-61.20E-52.93E-34.02E-4-1.19E-3accordance withNUREG0133,=Section4.3.1;andAlatorypositionC,Sectionl.'.1.69"'.71E-l'-4.36E-11.79E-14.60E-364 lp'l",>>'tIIg~'UQ","ht TABLE2-6AitVALUES-LIQUID*EMERGENCY CONDENSER VENTCHILD,mrem-mlhr-uCiLIVERTBODYTHYROIDKIDNEY1.44E-11.44E-l1.44E-l1.44E-lGI-TRACT1.44E-lLUNG1.44E-11.23E+22.638.88E+12.15E+31.03E+32.15E+26.14E+23.56E+42.38E-32.38E-36.00E+23.36E-33.36E-33.36E-31.99E-11.99E-11.99E-16.84E-33.61E+46.84E-34.09E+21.15E+31.01E+41.19E+33.07E+44.01E+53.01E-15.40E+36.84E+12.39E+16.75E+11.50E+21.67E+11.53E+19.61E-22.00E-16.06E-23.73E-21.74E+21.50f+23.08E+26.35E+11.50E+21.50E+21.06E+21.44E+12.50E-21.30E-26.71E+43.25E+37.67E+33.40E+39.66E+44.92E+55.77E+43.08E+31.30E-11.26E+22.17E-1'1.54E-22.39E-31.13E-46.83E-32.03E+21.45E+21.14E-31.90E+24.59E-21.55E-21.83E-S1.83E-55.15E-18.81E-26.36E-42.85E-1accordance withNUREG0133,Section4.latorypositionC,Sectionl.1.91E+13.75E+51.28E+31.34E+23.1;andRegulatory NUCLIDEBONEH3Cr513.78E-53.78E-51.377.58E-12.07f-l1.387.24E+1Cu641.59-6.35Mn541.23E-23.36E+38.95f+21.23E-29.42E+21.23E-22.82E+3fe559.04E+24.79E+21.49E+22.71E+2Fe591.28E+32.07E+3Co583.36E-37.01E+1Co601.99E-l2.08E+2Zn652.15E+45.73E+4"Sr898.78E+2Sr901.02E+5Zr956.78E-22.19E-32.19f-3Mn561.65f-lMo998.16f+12.02E+1Na241.50E+2l.'50E+21.50E+2I1311.86E+21.87E+26.19E+4I1333.08E+13.81E+17.07E+3Ni652.66E-11.46E-2---3.07I1326.01E-31.10E-25.08E-35.12E-11.69E-2Cs134"3"68E+56:04E+51.27E+56.29E-2.1.87E+5Cs1363.51E+46.25E+41.10E-35.14E+4Cs1375.14E+57.27E+49.55E-21.60E+5Ba1402.48E+21.45E+11.42E-47.09E-2Ce'1413.OBE-21.13E-4Nb955.21E+21.14E-3La1401.31f-l1.83E-5Ce1441.646.36E-4Calculated inGuide1.109,Regu65 IR'+vt>5>of~

'ITABLE2-7AitVALUES-LIQUID*EMERGENCY CONDENSER VENTTEEN,...mrem-mlhr-uCiTBODYTHYROIDGI-TRACTLIVERLUNGKIDNEY1.74E-lNUCLIDEBONEH3Cr511.81E-4Cu64Mn545.89E-2Fe.556.89E+2Fe591.05E+3Co581.61E-2Co609.53E-lZn652.10E+4Sr89'.'38E+4Sr904.54E+5Zr952.56E-lMn56Mo99Na'241.38E+2I1311.47E+2I1332.42E+1Ni652.08E-1I1324.86E-3's:134'"3!05E+5Cs1362.98E+4Cs1374.09E+5Ba1401.96E+2Ce-1412.43E-2Nb954.41E+2La1401.05E-1Ce1441.27*Calculated inGuide1.109,Regu1.74E-11.74E-11.74E-11.74E-11.74E-12.15E+22.81E-l1.831.81E-41.287.12E-l2.861.357.24-2.22E+21.28E+3-5.89E-2=-

-8.81E+33.10f+22.11E+24.29E+38.52E+25.89E-21.14f+24.88E+25.82E+31.21f+32.46E+38.78E+19.50E+21.14E-22.02E+21.61E-21.14E-27.76E21.61E-21.61E-29.53E-19.53E-14.66E+43.28E-22.57E+25.78E+29.53E-13.34E+33.08E+42.83E+37.28E+43.39E+43.28E-26.81E+21.12E+51.27E+48.80E-26'8E-21.05E-21.24E-l1.05E-21.79E+21.19E+11.54E+22.29E-11.96E+23.22E-21.81E-18.57E+11.63E+11.38E+21.38E+24.77E-44.07E+11.38E+2'.38E+21.38E+21.38E+23.54E+2.7.21E+12.06424.11E+11.10E+21.25E+16.00E+45.74E+33.11E+11.441.21E-22.66E-25.54E-34.56E-34.29E-1.2.00E-21.27E-2i'"7:18E+53.33E+5,3.01E-12.28E+58.71E+48.93E+36.38E+41.01f+49.43E+31.85E+57.19E+47.73E+38.23E-21.62E-l3.03E+28.02E-35.40E-44.54E+17.87E+45.28E-31.89E+54.57E-l1.27E+16.77E-42.36E-35.40E-41.15E+25.43E-31'.38E-2'.78E-57.12E-23.04E-31.17E+55.44E+52.47E-21.64E-2.2.45E+25.17E-25.28E-12.37E+28.78E-5'.17E-l5.43E-31.05E+68.78E-52.96E+3-3.04E-33.19E+2latorypositionC,Sectionl.accordance withNUREG0133,Section'4.3.1;andRegulatory 66 AS~l~IQ'kitSS'tSc, LOCATIONResidences DairyCowsfMilkGoatsfHeatAnimalsGardensSiteBoundary.DIRE(98')SE(130')SE(130')ESE(115')E(97')ENE(67')MILES1.42.62.61.81.80.4TABLE3-1CriticalReceptorDispersion Parameters>

ForGroundLevelandElevatedReleasesELEVATEDELEVATED~0/(m-X)5.2E-09b7.0E-10c7.0E-10c17E09c3.5E-09c44E08c,d~XI(sec/m3)1.8E-07b2.2E-08c2.2E-08c5.1E-08c10E07c~24E-06b,dGROUNDeXA/(sec/m~)

4.02E-076.00E-086.00E-081.16E-072.53E-076.63E-06GROUNDeD/(/(mX)8.58E-091.64E-091.64E-0983.54E-095.55E-096.35E-08a.Thesevalueswillbeusedindosecalculations beginning inApril1986butmayberevisedperiodically toaccountforchangesinlocations offarms,gardensorcriticalresidences.

b.Valuesbasedon5yearannualmeteorological data(C.T.Main,Rev.2)Ic.Valuesbasedon5yearaveragegrazingseasonmeteorological data(C.T..MainRev.2)d.Valuearebasedonmostrestrictive X/9land-based sector(ENE).(C.T.Hain,Rev.2)e.Valuesarebasedonaverageannualmeteorological datafortheyear1985.f.Conservative locationbasedonpastdairycowandgoatmilkhistory.68

'ClIIlÃgLft1 NuclideKr-85Kr-85mKr-87Kr-88Kr-89Kr-83mXe-133Xe-133mXe-135Xe-135mXe-137Xe-138Xe-131mAr-41TABLE3-2GammaAirandWholeBodyPlumeShineDoseFactors'or NobleGasesGambiaAirBi~mrad/ruCi/sec2.23E-61.75E-31.02E-22.23E-22.50E-22.26E-62.80E-42.27E-42.62E-35.20E-32.30E-31.32E-21.74E-S1.64E-2GammaWholeBodyVim~rem/ruCi/sec1.68E-39.65E-32.17E-22'1E-41.87E-42.50E-34.89E-32.20E-31.26E-21.47E-61.57E-2*Calculated inaccordance withRegulatory Guide1.109.(SeeAppendixB) kf-4gf TABLE3-3IMMERSION DOSEFACTORS*NuclideK>~(l-Bad>'"Li(6-Skin)**

H>~(-Alr>***N>0>-A>r>*'*

Kr83mKr85mKr85Kr87Kr88Kr89Kr90Xe131mXe133mXe133Xe135mXe135Xe137Xe138Ar417.56E-021.17E31.61El5.92E31.47E41.66E41.56E49.15El':51E22.94E23.12E31.81E31.42E38.83E38.84E31.46E31.34E3'9.'73E32.37E31.01E47.29E34.76E29.94E23.06E27.11EZ1.86E31.22E44.13E32.69E31~93E11.23E31.72E16.17E31.52E41.73E41.63E41.56E23.27E23.53E23.36E3'1.92E31.51E39.21E39.30E32.88E21.97E31.95E31.03E42.93E31.06E47.83E31.11E31.48E31.05E37.39E22.46E31.27E44.75E33.28E3*from,TableB-l.Regulatory Guide1.109Rev.1~**mrem/yr peruCi/m.***mrad/yr peruCi/m.70

~'5%.A<~c>lh~1%I NUCLIDE..BONETABLE3-4RiVALUES-INHALATION

-INFANT*~mremlruCi/mLIVER,T.BODYTNYROIDKIDNEYLUNGGI-LLIH3C14Cr51Mn546.47E26.47E26.47E22.65E45.31E35.31E35.31E38.95E1.5.75E12.53E44.98E36.47f26.47E26.47E25.31E35.31E35.31E31.32El1.28E43.57f24.98E31.00E67.06E3Fe551.97E41.17E43.33E3Fe591.36E42.35E49.48E3Co58Co601.22E31.82E38.02E31.18E4"Zn"65'.93E4-6.26E4"'3.11E4 8.69E41.09E31.01E62.48E47.77E51.11E44.51E63.19E43.25E46.47E55.14E4Sr893.98ESSr904.09f71.14E42.59E62.03E66.40E41.12E71.31E5Zr951.15E52.79E42.03E4*Nb951.57E46.43E33.78E3Mo99I1313.79E41.65E24.44f43.23E11.96E41.48E7'La1405.05E2'.00E25.15E1Ce1412.77E41.67E41.99E3Ce1443.19E61.21E61.76E5Nd1477.94E38.13E3,5.00E2I1331.32E41.92E45.60E33.56E6Cs1343.96ES7.03f5'.45E4Cs1375.49E56.12E54.55E4Ba1405.60E45.60E12.90E33.11E41.75E62.17E44.72E34.79E51.27E42.65E21.35ES4.87E45.18E42.24E41.06E32.16E31.34El1.60E63.84E41.68E58.48E45.25E35.17E52.16E45.38E59.84E61.48E53.15E33.22E53.12f41.90ES7.97E41.33E31.72E57.13E41.33E3*Daughter DecayProduct.**Thisandfollowing RiTablesCalculated inaccordance withNUREG0133,Section5.3.1,exceptC14valuesinaccordance withRegulatory Guide1.109EquationC-8.71 N"1I>>

TABLE3-5R)VALUES-INHALATION

-CHILDm~remlruCf/mNUCLIDEBONELIVERT.BODYTHYROIDKIDNEYLUNGGI-LLIH31.12E31.12E31.12E31.12E31.12E31,12E3C143'9E46.73E36.73E36.73E3.6.73E36.73E3.6.73E3"Cr51'1.54E28:55E12.43E11.70E41.08E3Hn544.29E49.51E31.00E41.58E62.29E4Fe554.74E42.52E47.77E3Fe592.07E43.34E41.67E4Co'58Co601.77E33.16E31.31E42.26E4Zn654.25E41.13ES7.03E41.11E52.87E31.27E67.07E41.11E63.44E47.07E69.62E47.14E49.95E51.63E4Sr895.99E5Sr901.01EBZr951.90E5*Nb952.35E4Ho994.18E49.18E31.72E46.44E63.70E46.55E31.72E24.26El2.16E61.67E51.48E73.43E55.96E42.23E66.11E48.62E36.14E53.70E43.92E21.35ES1.27E5I1314.81E44.81E42.73E41.62E77.88E4I1331.66E42.03E47.70E33.85E63.38E42.84E35.48E3Cs134Cs1376.51ES1.01E62.25E59.07E5'8.25E5,1.28E5Ba1407.40E46.48E14.33E3*La1406.44E22'5E27'SElCe1413.92E41.95E4-2.90E3'Ce1446.77E6.2.12E63.61E5Nd1471:OBE4'8.73E36.81E23.30E51.21E53.85E32.82E51.04E53.62E32.11E11.74E6.1.02E51.83ES2.26E58.55E35.44E55.66E41.17E61.20E73.89ES4.81E33.28E58.21E4*Daughter DecayProduct.72 IJI~aII~IfIf~II-I-"I~'III"I'III*'f4rI~I TABLE3-6RtVALUES-INHALATION

-TEEN~mremlruC)/mNUCLIDE"BONELIVERT.BODYTHYROIDKIDNEYLUNGGI-LLIH3-1.27E31.27E3l.'27E31.27E31.27E31.27E3C142.60E44.87E34.87E3'4.87E34.87E34.87E3'4.87E3CrSl1.35E27.50E13.07E1'.10E43.00E3Mn54-5.11E4Fe553.34E42.38E4Fe591.59E43.70f4Co58-'.07E38.40E35.54E31.43E42.78E3Co60-1.51E41.98E4Zn653.86E41.34E56.24E41.27E41.98E66.68E41.24fS6.39E31.53E61.78E51.34E69.52E4'.72E6 2.59E58.64E41.24E64.66E4Sr894.34f5Sr901.08EBZr951.46E54.58E4*Nb951.86E41.03E4Mo99--1.69E21.25E46.68E63.15E45.66E33.22El2.42E63.71E51.65E77.65fS6.74E42.69E61.49E51.00E47.51ES9.68E44.11E21.54E52.69E5I1313.54E44.91E42.64E41.46E78.40E4I1331.22E42.05E46.22E32.92E63.59E46.49E31.03E4Cs1345.02E5Cs1376.70E51.13E65.49E58.48E53.11E5Ba1405.47E46.70El3.52E3*La1404.79E22.36E26.26ElCe1412.84E41.90E4"2.17E3Ce1444.89E62.02E62.62ESNd1477.86E38.56E3513E2*Daughter DecayProduct.733.75ES1.46E59.76E33.04E51.21E58.48E32.28E12.03E62.29ES2.14E54.87ES8.88E36.14E51.26E51.21E61.34E78.64E55.02E33.72E51.82E5

~r'~fbiJ TABLE3-7R)VALUES-INHALATION

-AOULT~mremlruC)/mNUCLIDEBONELIVERT.BODYTHYROIDKIDNEYLUNGGI-LLI"C14'.82E43.41E3"Cr513.41E3'.41E33.'41E31.00E25.95E12.28E1H31.26E3'.26E31.26E31.26E31.26E33.41E31.26E33.41E3"1.44E43.32E3Co58-1.58E3Co60-1.15f4'.07E31.48E4Zn653.24f41.03ES4.66f4MnS4-3.96E46.30E3Fe552.46f41.70E43.94E3FeS91.18E42.78E41.06E49.84E31.40E67.74E47.21E46.03E31.02E61.88ES9.28E51.06E55.97E62.85E56.90E48.64E55.34E4Sr893.04E5Sr90'.92E7Zr951.07ES*Nb951.41E43.44E47.82E38.72E36.10E62.33E44.21E37.74E35.05E51.04E51.40E63.50E59.60E67.22E55.42E41.77E61.50E5Mo991.21E22.30E12.91E29.12E42.48ESI1312.52E43.58E42.05E41.19E76.13E4I1338.64E31.48E44.52E32.15E62.58E46.28E38.88E3Cs1343.73ESCs1374.78E58.48E57.28ES6.21ES4.28E5Ba1403.90E44.90El2.57E3'La1403.44E21~74E24.58E1Ce1411.99E41.35f41.53E3Ce1443.43E61.43E61.84ES'Nd'147'.27E36.10E3'3:65E2*Daughter OecayProduct.742.87ES9.76E41.04E42.22E57.52E48.40E31.67E11.27E62.18E51.36ES4.58ES6.26E33.62ES1.20E58.48E57.78E68.16E53.56E32.21E51.73E5 FliCsQ~-'I TABLE3-8R)VALUES-GROUNDPLANEALLAGEGROUPSm~mremlr2uC)/secNUCLIDEH3C14Cr51Hn54Fe55Fe59Co58Co60Zn65"Sr89Sr90Zr95*Nb95Ho99I131I133Cs134Cs137Ba140:*La1.40Ce141Ce144Nd147..*Daughter DecayProduct.TOTALBODY4.68E61.39E92.75E83.82E82.15E107.49E82.26E42.50E81.36EB4.04E61.72E72.39E66.81E91.03E102.06E7,1.92E71.37E76.95E78.46E6SKIN5.53E61.63E93.23EB4.47E82.53E108.62E82.62E42.90E81.61E84.67E62.09E72.91E67.94E91.20E102.35E72.18E71.54E78.03E71.01E775 tr NUCLIDEBONELIVERTABLE3-9R)VALUES-CONMILK-INFANTm~mremlruCi/secT.BODYTHYROIDKIDNEYLUNGGI-LLI*H3-3.10E33.10E33.10E33.10E33.10E33.10E3*C143.23E66.89E56.89E56.89E56.89E56,89E5.'6.89E5Cr518.37E4,5.46E4.1.19E41.06E52.44E69.22E6Mn54-2.51E75.69E6Fe558.98E75.80E71.55E7Fe591.22EB2.14ES8.42E7Co58-1.39E73.47E75.56E62.83E77.36E66.31E71.02EB3.47E71.40E8'.02E10 1.45E81.02E94.71E51.09E83.47E75.73E74.20E6Co605.90E71.39E8Zn653.53E91.21E105:58E95.87E92.02E&2.09E10Sr897.04E9Sr908.19E10Zr953.88E39.45E26.70E2*+Nb953.14E51.29E57.48E4Mo99-1.05E82.06E71.02E39.27E41.58E8I1331.70E72.48E7Cs1342.41E104.49E107.27E64.51E92.92E71.16E104.74E91.22EB1.09E104.41E91.27E82.87E47.42E42.97E74.54E92.88E96.23E6Cs1373.47E104.06E10Ba1401;21E81.21E5I1311.36E91.60E97.06E85.27E111.87E+9**La1402;03El7.99Ce1412.28E41.39E4Ce1441.49E66.10E52.061.64E38.35E4Nd1474.43E2.4.55E22.79E1*mrem/yrperuCI/m3.**Daughter DecayProduct.764.29E32.46E51.76E29;39E4-7.18E68.55E72.89E5

NUCLIOEBONELIVERTABLE3-10RiVALUES-CONMILK-CHILDm~mremlr2uCi/secT.BODYTHYROIDKIDNEYLUNGGI-LLI*H3-2.05E32.05E32.05E32.05E32.05E32.05E3*C141.65E63.29E53.29E53.29f53.29E53.29E53.29E5Cr515-29E42.93E48.02E35.36E42.&OE6Mn54-1.35E73.59E6Fe557.43E73.94E71.22E7Fe596.55E71.06EB5.28E7Co58-6.96E62.13E73.78E6Co602.89E78.52E7Zn652.63E97'OE94.35E94.41E9Sr893.70E9SI907.53E101.06EB1.91E10Zr952.18E34.&OE24.27E2**Nb951.6&E56.55E44.68E4Mo994.13E71.02E76.87E26.15E48.81E7I131.6.52EB6.56EB,3.73EB2.17Ell1.08E9I1338.07E69.98E63.78E61.85E91.66E71.13E72.23E77.30E63.07E71.10E&4.06E71.60EB1.23E91.43EB1.01E95.01E51.21EB3.41E75.84E74.02E6Cs1372.17E102.08E10Ba1405.&BE75.15E43.07E93.43f6Cs1341.50f102.46E105.18E97.61E92.73E91.32E&6.78E92.44E91.30EB1.68E43.07E42.98E7.**La1409.703.391.14Ce1411.15E45.74E38.52E25.55E41.40EICe1441.04E63.26E5Nd1472.24E21.8lf2e*mrem/yrperuCi/m3.**Daughter OecayProduct.772.51E31.80E59.94E19.45E47.15E68.50E72.87E5 0AT\>r44A44 TABLE3-11RiVALUES-CONMILK-TEENm~mrem/r2uCi/secNUCLIDEBONELIVERT.BODYTHYROIDKIDNEYLUNGGI-LLI*H31.29E31.29E31.29E31.29E31.29E31.29E3'C146.70E51.34E51.34E51.34E51.34E51.35E51.34E5Cr512.59E41.44E45.68E33.70E44.35E6Mn549.02E61.79E6Fe552.96E72.10E74.89E6Fe592.82E76.59E72.55E72.69E61.85E71.33E79.08E62.08E71.56EBCo584.55E61.05E7Co601.86E74.19E7Zn651.34E94.65E92.17E92.98E9Sr891.50E9Sr904.46E104.28E71.10E10Zr959.40E22.97EZ2.04E2**Nb957.45E4Mo994.13E42.27E72.27E44.32E64.36E24.01E45.19E7,I1312.69EB*3.77EB2.02E81.10E116.48EBI1333.32E65.64E61.72E67.87E89.88E66.28E72.42E81.97E91.78E81.25E96.85E51.77E84.06E77.45E74.26E6Cs1346.49E91.53E107.08E9Cs1379.02E9,1.20EIOBa1402.43E72.98E4**La1404.051.994.18E91.57E65.30E-1Ce1444.22E51.74E5Nd1479.12E19.91E1*mrem/yrperuCi/m3.**Daughter DecayProduct.2.27E45.94EOCe1414.67E33.12E33.5&E2784.85E91.85E94.08E91.59E91.90E8i1.71EB1.47E31.04E55.82E11.14E58.92f61.06E83.58E51.01E42.01E43.75E7 I'~iJl~~'

TABLE3-12RiVALUES-CONHILK-ADULTm~mremlr2uCi/secNUCLIDEBONELIVER*H39.94E2T.DODYTHYROIDKIDNEYLUNG9.94E29.94E29.94E29.94E2GI-LLI9.94E2*C143.63E57.26E4:.7.26E47.26E47.26E47.26E47.26E4Cr511.48E48'7E33.27E31.97E43.73E6Hn54-5'1E61.03E6Fe551.67E71.15E72.69E6Fe591.62E73.80E71.46E7Co582.70E66.06E6Co601.10E7'2.42E7Zn658.72E82.78E91.25E91.61E61.86E9Sr898.11E8Sr903.15E102.33E77.74E9Zr955.38E21.72E21.17E2**Nb954.37E42.43E41.31E4Ho991.26E72.39E62.71f22.40E42.84E7I1311.48E8;2.12E8=.1.22E8~6.95E103.63E8I1331.82E63.16E69.64E54.65E85.52E61.66E76.43E66.6lf61.06E71.27E85.48E72.06E81.75E91.30E89.11E85.47E51.47E82.91E75.59E72.84E6Cs1343.74E98.89E97.27E9Cs1374.98E96.80E9Ba1401.35E71.69E4**La1402.261.144.46E98.83E53.01E-1Ce1412.55E31.72E31.95E2Ce1442.29fS9.58E4'.23E4Nd1474.74E15.48E13.28EO*mrem/yrperuCi/m3.**Daughter DecayProduct.798.00E25.68E43.20E18.35E46.58E67.75E72.63f52.88E99.55E81.56E82.31E97.68E81.32E85.76E39.70E32.78E7 Qlt~7f~

TABLE3-13RiVALUES-GOATMILK-INFANTm~mremlruCi/secNUCLIDEBONELIVERT.BODYTHYROIDKIONEYLUNGGI-LLI<<H36.33E36.33E36.33E36.33E36.33E36.33E3*C143.23E66.89E5.6.89E5.6.89E56.89E56.89E56.89E5Cr511.00E46.56E31.43E31.28E42.93E5Mn54-3.01E66.82f5Fe551.17E67.54E52.01E5Fe591.59E62.78E61.09E6.Co58-.1.67E6.4.16E6Co60-7.08E61.67E7Zn654.24E81.45E96.70E86.67E57.04E8Sr891.48f10Sr90.1.72E114.24E84.38E10Zr95'.66E21.13E28.04EI1.22E21.11E41.89E7**Nb953.77E41.55E48.97E32.47E6Mo99-1.27f7le"I'131--1.63E9-',1.93E9'.47EB,6.33E112.25E9-I1332.05E72.98E78.72E65.42E93.50E71.11E63'9E5,9.57E48'1E51.33E64.16E61.68E71.23E93.04E82.15E95.65E41.31E74.17E66.87E75.04E6Cs1347.23E101.35E111.36E10..Cs1371.04E11"1.22E118.63E9Ba1401.45E71.45E4'7.48E5**La1402.4309.59E-l2.47E-lCe1412.74E31.67E31.96E2Ce1441.79E57.32E41.00E4Nd1475.32E15.47E13.35EO*mrem/yrperuCi/m3.'*Daughter DecayProduct.805.14f22.96E42.11El1.13E48.62E51.03E73.46E43.47E101.42E103.66E83.27E101.32E103.81E83.44E38.91E33.56E6 f4~W,iiIiA'*ifI~:ffk/i~'f~'"~<LQ'~)fIfgiffQ, NUCLIDEBONELIVERTABLE3-14RiVALUES-GOATMILK-CHILDm~mremlruCi/secT.BODYTHYROIDKIDNEYLUNGGI-LLI*H3-4.17E34.17E34.17E34.17E34.17E34.17E3*C141.65E63.29E53.29E53.29ES3.29E53.29E53.29E5Cr516.34E33.52E39.62E26.43E33.36E5Hn54-1.62E64.31E5Fe559.65E55.12E51.59E5Fe598.52E51.38E66.86E5Co58-8.35E52.56E6Co603.47E61.02E74.54E51.36E62.90E59.49E43.99E51.43E64.87E61.92E7Zn653.15E88.40EB5.23EB5.29E8Sr897.77E9Sr90.1.58E112.22E84.01E10Zr952.62E25.76E15.13El**Nb952.02E47.86E3Mo994.95E65.62E31.22E6..I131..7.83EB..7.87EB.4.47EB8.25E17.38E31.06E7,2.60E111.29E9I1339.69E61.20E74.53E62.23E92.00E71.48E83.01E82.13E96.01E41.45E74.09E67.01E74.83E6.Cs1376.52E10..6.24E10Ba1407.05E66.18E39.21E94.12E5Cs1344.49E107.37E101.55E102.28E108.19E93.97E82.03E107.32E93.91E82.01E33.68E33.57E6**La1401.164.07E-11.37E-11.13E4Ce1441~25E53.91E4Nd1472.68E12.17E1*mrem/yrperuCi/m3.**Daughter DecayProduct.6.66E31.68EOCe1411.38E3-6.88E21.02E2813.02E22.16E41.19E18.59E51.02E73.44E4 AAIIIrpAVf TABLE3-15RiVALUESGOATMILKTENm~mremlruCi/secNUCLIDEBONELIVERT.BODYTHYROIDKIDNEYLUNG*H3-'.64E32.64E32.64E32.64E32.64E3*C146.70E51.34E51..34E51.34E51.34E51.35E5GI-LLI2.64E31.34E5.Cr513.1.1E31.73E3...6.82E2 4.44E3.5.23E5Mn541.08E62.15E5Fe553.85E52.73E56.36E4Fe593.67E58.57E53.31E5Co58-5.46E51.26E6Co602.23E65.03E6Zn651.61E85.58E82.60EB3.23E53.57E8Sr893.14E9Sr909.36E108.99E72.31E10,Zr951.13E23.56El2.45E1**Nb958.94E34.96E3~~Mo992.72E62.73E35.19E55.23E'14.81E36.23E6II131:'.3.23E8 R4.52EB.2.43E81.32E117.78EBI1333.99E66.76E62.06E69.44E81.19E72.22E61.73E51.18E52.70E52.03E67.53E62.91E72.36E83.74E82..63E98.22E4'2.12E74.87E68'4E75.12E6.Cs1372.71E10..3.60E10Ba1402.92E63.58E31.25E101.88E5Cs1341.95E104.58E102.13E101.46E105.56E95.70EB1.23E104.76E95.12EB1.21E32.41E34.50E6Ce1445.06E42.09E4Nd1471.09El1.19El*mrem/yrperuCi/m3.**Daughter DecayProduct.2.72E37.13E-1**La1404.86E-12.39E-l6.36E-2Ce1415.60E23.74EZ4.30El821.76E21.25E46.99EO1.37E41.07E61.27E74.29E4

~4.kjg\~AI'lF4 TABLE3-16R)VALUES-GOATMILK-ADULTm~mremlruCl/secNUCLIDEBONELIVERT.BODYTHYROIDKIDNEYLUNGiGI-LLI*H3.-2.03E32.03E32'3E32.03E32.03E32.03E3*C143.63E57.26E47.26E47'6E47.26E47.26E47.26E4Cr511.78E31.06E33.92E22.36E34.48E5Mn546.50E51.24E5Fe552.17E51.50E53.49E4Fe592.10E54.95E51.90E5Co58-.-3.25E5,7.27E5Co60-1.32E62.91E6Zn651.05E83.33E81.51E81.93E52.23EBSr891.70E9Sr906.62E10Zr956.45E12.07E1**Nb955.24E32.92E3Mo991.51E6~qI13141:78E8".,2.54EB4.89E71.63E101.40E11.57E32.87E53.25EI2.88E33.41E6~1.46E8.8.34E104.36EBI1332.18E63.80E61.16E65.58EB6.62E61.99E68.36E4860E41.38E51.65E66.58E62.48E72.10E82.73E81.91E96.56E41.77E73.49E66.71E73.41E6Cs1341.12E102.67E102.18E10.Cs1371.49E10"2.04E101.34E10Ba1401.62E62.03E31.06E5**La1402.71E-l1.36E-13.61E-2Ce1413.06E22.07E22.34E1Ce1442.75E41.15E41.48E3Nd1475.69EO6.57EO3.93E-1*mrem/yrperuCf/m3.**Daughter DecayProduct.839.60E16.82E33.84EO1.00E47.90E59.30E63.15E48.63E92.86E94.67E86.93E92.30E93.95E86.91EZ1.16E33.33E6 Iqp)'I1~~C'I~44 NUCLIDEBONELIVERTABLE3-17RiVALUES-COWMEAT-CHILDm~mremlr2uCi/secT.BODYTHYROIDKIDNEYLUNGGI-LLI*H33.04EZ3.04E23.04E23.04E23.04E23'4E2*C145.29ES1.06E51.06E5.1.06E5.1.06E51.06E51.06E5Cr514'.57E32.54E36.93E24.63E32.42E5Mn545.36E61.43E6Fe553.04ES1.61EB4.99E7Fe592.06E83.33E81.66ESCo589.43E62.89E7Co60-4.67E71.38ESZn652.39ES6.36E83.96E81.50E64.01E8Sr892.72ESSr907.01E97.77E61.78E9Zr951.53E63.35E52.98E5**Nb951.64E6Mo996.38E56.11E44.56E51.51E44.80ES5.99E51.31E5I1331.88E-12.32E-18.78E-24.31E13.87E-1I,131,8.30E6<<8.35E6--4.75E62.76E91.37E74.50E69.11E72.98E79.64E73.46ES5.50E72.59E81.12E81.05E79.44E73.50E81.18E95.06E47.43E59.35E-2Cs1378.99E88.60E8Ba1402.20E71.93E41.27ES1.28E6Cs1346.09E81.00E92.11ES3.10ES1.11ES5.39E62.80ES1.01ES5.39E66.28E31.15E41.12E7**La1402.80E-2'.78E-33.30E-3Ce1411.17E45.82E38.65E2Ce1441.61E65.04E5"8.57E4Nd1475.93E34.80E33.72E2*mrem/yrperuCi/m3.**Daughter DecayProduct.842.55E32.79E52.64E32.73E27.26E61.31E87.61E6

~CCL.I~CIC NUCLIDEBONELIVERTABLE3-18RtVALUES-CONHEAT-TEENm~mremlr2uCi/secT.BODYTNYROIOKIDNEYLUNGGI-LLI'H3-2.52E22.52E22.52E22.52E22.52E22.52E2*C142.81E55'2E45.62E4.5.62E45'2E4,5.62E4,.5..62E4 Cr512.93E31.63E36.42E24.19E3Hn54-4.69E69.30E5Fe551.58ES1.12ES2.62E7Fe591.16ES2.71ES1.04ESCo58-8.07E61.86E7.Co603.93E78.86E7Zn651.59E85.52ES2.58ES1.40E63.54E87.12E78.53E7Sr891.44E8Sr905.42E94.12E61.34E9Zr958.59E52:71E51.86E5**Nb959.49E55.26E52.90E5Ho994.39E48.38E33.98E55.10ES1.01E5I1331.01E-11.71E-15.23E-22.39E13.00E-1I.131m04.48E66.27E63.37E6-1.83E91.08E74.93E59.62E64.86E76.40E81.11ES5.12E82.34E81.71E71.52E86.25E82.25E97.87E41.24E61.30E-1Cs1374.88E86.49E8Ba1401.19E71.46E42.26E87.69E5Cs1343.46ES8.13ES3.77ES2.58E89.87E7'1.01E72.21E88.59E79.24E64.96E39.83E31.84E7Ce1448.52E53.53E5Nd1473.16E33.44E3*mrem/yrperuC)/m3.**Oaughter OecayProduct."4.58E42.06E2**La1401.53E-27.51E-32.00E-3Ce1416.20E34.14E34.76E285.1.95E32.11E52.02E34.31E21.18E72.14ES1.24E7 C,

NUCLIDEBONELIVERTABLE3-19RiVALUESCONHEATADULTm~mremlruCi/secT.BODYTHYROIDKIDNEYLUNGGI-LLI'H3-4.22f24.22E24.22E24.22E24.22E24.22E2*C143.33E56.66E46.66E46.66E46.66E46.66E46.66E4Cr51'3.67E32.19E3.8.08E24.86E3..9.22E5Mn54-6.15E61'.17E6Fe551.95ES1.36ES3.14E7Fe591.45ES3.4lfS1.31ESCo58-1.05E72.35E7Co60-5.07E71.12fSZn652.26ES7.20ES3.25ES1.83E64.81ESSr891.70E8.Sr908.38E94.89E62.06E92r951.07E63.44E52.33E5**Nb951.22E66.76E5Ho99-5.31E43.63ES1.01E45.40E56.68ES1.20E5*I131'.39E6,7.71E6,:4.42E6.2'3E91.32E7I1331.21E-12.10E-16.40E-Z3.09E13.66E-11.88E77.51E77.72E79.53E71.14E92.12E89.52E84.53E82.73E72.42E81.09E94.10E91.23E52.03E61.89E-1,Cs1375.88E8..8.04E8Ba1401.44E71.81E45.27ES9.45E5Cs1344.35ES1.03E98.45E83.35E81.11ES1.81E72.73E89.07E71.56E76.16E31.04E4.2.97E7Ce1441.01E64.23E5Nd1473.59E34.15E3*mrem/yrperuCi/m3.'*Daughter DecayProduct.5.43E42.48f2**La1401.86E-29.37E-32.48E-3Ce1417.38E34.99E35.66EZ862.32E32.51E52.42E36.88EZ1.91E73.42ES1.99E7 l~~~Ai~

TABLE3-20RiVALUES-VEGETATION

-CHILDm~Nrem/ruC1/secNUCLIDEBONELIVERT.BODYTHYROIDKIDNEYLUNGGI-LLI*H3-5.22E35.22E35.22E35.22E35.22E35.22E3*C143.50E67.01E5'.01E57;01ES'.01ES7.01E57.01E5Cr511.18f5'*6;54E4.79E4 1.19E56.25E6Mn54-6.65E81.77E81.86E85.58E8Fe558.01E84.25E81.32E8Fe594.01f86.49E83.23E8Co586.47E7Co60-'.78E81.98E81.12E9ZA658.13E82.17E91.35E91.36E92.40E87.87E71.88E86.76E83.77E82.10E93.80E8Sr893.74E10Sr901.24E121.07E93.15E11Zr953.92E68.63E57.68ES**Nb954.10ES1.60E51.14E5Mo997.80E61.93E61.23E61.50ES1.67E7mI131'1.43E81.44E88.18E74.76E102.36E8I1333.39E64.19E61~58E67.78E86.98E61.45f91.67E109.00E82.95E86'5E61.28E71.69E6Cs1372.39E102.29E10Ba'402.77EB2.43E53.38E9'1;62E7Cs1341.60E102.63E105.55f98.15E92.92E91.42E87.46E92.68E91.43E87.91E41.45E51.40EBCe1441.27EB3.98E7Nd1477.23E45.86E4*mrem/yrperuC1/m3.**Daughter OecayProduct."6.78E64.54E3**La140'3.'25E3 1.13f33.83E2Ce1416.56ES3.27E54.86E4871.43E52.21E73.22E43.16E74.08EB1.04E109.28E7 4

TABLE3-21RlVALUES-VEGETATION-m~mremlruCi/secTEENNUCLIDEBONELIVERT.BODYTHYROIDKIDNEYLUNGGI-LLI'H3-3.37E3.3.37E33.37E3,3.37E33.37E33.37E3'C141.45E62.91E52'1E52.91E52.91E52.91E5.2.91E5Cr516.20E43.44E41.36E48.85E41.04E7Mn54-4.55E89.01E7Fe553.26ES2.31ES5.39E7Fe591.81ES4.22ES1.63E81.36ES'.32E81.47E81.00E81.33EB9.99EBCo58-4.38E71.01E8Co60-2.49ES5.60ESZn654.24E81.47E96.87E89.42ESSr891.57E10Sr90.7.51Ell4.50ES1.85E118.11E51.03E51.31E7Zr951.75E65.52E53.80E5**Nb951.92E51.06E55.86E41.09E6Mo995.71E6"I131,".7.70E7.1.08E8-5.79E7.3.14E101.86EBI1331.86E63.15E69.61E54.40ES5.52E66.04EB3.24E96.24EB1.87E92.11E101.27E94.55EB1.02E72.13E72.38E6Cs1371.01E10..1.35E10Ba1401.38EB1.70E54.69E98.91E6Cs1347.10E91.67E107.75E95.31E92.03E92.08EB4.59E91.78E91.92EB5.75E41.14E52.13EB**La1401.81E38.88E22.36E2Ce1412.83E51.89E52.17E4Ce1445.27E72.18E72.83E6Nd1473.66E43.98E42.38E3*mrem/yrperuCl/m3**Daughter DecayProduct.888.90E41.30E72.34E45.10E75.41EB1.33E101.44E8 t'))l%VI~iiflit~lV)V(~F-4t)II*<)')<<rkiP A)~CAajtt)leitE'l TABLE3-22RiVALUES-VEGETATION

-ADULTm~mrem/r2uCi/secNUCLIDEBONELIVERT.BODYTHYROIDKIDNEYLUNGGI-LLI*H3-2.26f32.26E32.26E32.26E32.26E32.26E3*C148.97ES1.79E51.79E5.1.79E51,79E51.79E5.1.79E5Cr514.67E42.79E41.03E46.'19E41.17E7Mn54-3.13f85.97E7Fe552.10ES1.45ES3.38E7Fe591.27ES2.99ES1.15E89.31E79.59f88.08E78.31E78.35E79.96E8Co58-,3.09E76.92E7Co60-1.67E83.69ESZn653.18E81.01E94.57E86.76ESSr891.03E10Sr906.04Ell2.96E81.48E11Zr951.19E63.83E52.59E5*Nb951.42ES.7.91.E4Mo99-6.22E64.25E41.18E66.00E57.82E41.41E7I'1318;09E7',1.16ES6.63E73.79E101.98ESI1332.00E63.48E61.06E65.11ES6.07E66.26EB3.14E96.36EB1.65E91.75E101.21E94.80ES1.44E73.05E73.13E6Cs1344.66E91.11E109.07E93.59E91.19E91.94EB.Cs1376.36E9..8.70E9Ba1401.29ES1.62ES5.70f98.43E6Ce1443.29E71.38f7Nd1473.36E43.88E4*mrem/yrperuCi/m3**Daughter DecayProduct.1.77E62.32E3**La1401~98E39.97E2.2.63E2Ce1411.97E51.33ES1.51E4&92.95E95.49E46.19E48.16E62.27E49.25E42.65ES7.32E75.10EB1.11E101.86E89.81EB1.68f8 I'I1lk.w4C4,'I$hf5.ge"*F8"~'*VI~CE NineMilePointNuclearStationRadiological Environmental Monitoring ProgramSamplingLocations Table5.1TypeofSamleRadioiodine andParticulates (air)Radioiodine andParticulates (air)Radioiodine andParticulates (air)Radioiodine andParticulates (air)Radioiodine andParticulates (air)*MapLocation(Env.Collection SiteProramNo.)LocationNineMilePointRoadNorth(R-1)1.8mi988'Co.Rt.29(R-3)1.5mi9132'.SEVillageofLycoming, NY(R-4)1.8mi8143'EHontarioPointRoad(R-5)16.4mi942'ECo.Rt.29&LakeRoad(R-2)1.1mi8104'SE"Direct'Radiation

'(TLD)'6DirectRadiation (TLD)7DirectRadiation (TLD)8DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)10ll12DirectRadiation (TLD)13DirectRadiation (TLD)'4DirectRadiation (TLD)15DirectRadiation (TLD)16Direct'Radiation (TLD)17DirectRadiation (TLD)18NorthShoreline Area(75)NorthShoreline Area(76)NorthShoreline Area(77)NorthShoreline Area(23)JAFEastBoundary(78)Rt.29(79)Rt.29(80)HinerRoad(81)MinerRoad(82)LakeviewRoad(83)LakeviewRoad(84)0.1mi95'~0.1mi925'NE0.2mi945'E0.8mi970'NE1.0mi990E1.1mi9115'SE1.4mi8133'E1.6mi9159'SE1.6mi8181'1.2mi9200'SW1.1mi8225'WSiteMeteorological Tower(7)0.7mi9250WSWEnergyInformation Center.(18)0.4mi.8265;W;*Map-SeeFigures5.1-1and5.1-2 hI~I4E.0)~CjFc' NineMilePointNuclearStationRadiological Environmental Monitoring ProgramSamplingLocations Table5.1(Continued)

TypeofSamle'MapLocation(Env.Collection SiteProramNo.)LocationDirectRadiation (TLD)19DirectRadiation (TLD)20DirectRadiation (TLD)21DirectRadiation (TLD)22DirectRadiation (TLD)23DirectRadiation (TLD)24DirectRadiation (TLO)25'DirectRadiation.(TLD),

26DirectRadiation (TLD)27DirectRadiation (TLO)28DirectRadiation (TLO)29DirectRadiation (TLD)30DirectRadiation (TLD)31DirectRadiation (TLD)32DirectRadiation (TLO)33DirectRadiation (TLD)34DirectRadiation

<TLD)35DirectRadiation (TLD)36Direct'adiation (TLD)37SurfaceWater38SurfaceHater39NorthShoreline (85)NorthShoreline (86)-NorthShoreline (87)HickoryGrove(88)LeavittRoad(89)Rt.104(90)Rt.51A(91)MaidenLaneRoad(92)Co.Rt.53(93)Co.Rt.1(94)LakeShoreline (95)Phoenix,NYControl(49)S.W.Oswego,Control,(14)Scriba,NY(96)AlcanAluminum, Rt.1A(58)Lycoming, NY(97)NewHaven,NY<56)0.2mi9294'NH0.1mi8315NW.0.1mi8341.'NNW4.5mi997,E,4.1mi8ill'SE4.2mi9135'E4.8mi8156'SE4.4mi8183'4.4mi9205'SH4.7mi9223'H4.1mi8237WSH~19.8mi8170'12.6mi8226SH3.6mi8199'SH3.1mi9220'H1.8mi8143'E5.3mi9123'SELakeRoad(98)OSSInletCanal(NA)JAFNPPInletCanal(NA)1.2mi9101'7.6mi9235'H0.5mi870'NEH.Boundary, BibleCamp(15)0.9mi8237'SH(NA)notapplicable

  • MapSeeFigures5.1-1and5."l-2 w'th7pV NineMilePointNuclearStationRadiological Environmental Monitoring ProgramSamplingLocations Table5.1(Continued)

TypeofSamle*MapLocation(Env.Collection SiteProramNo.)Location'horeline SedimentFishFishFishHilkMi1kMi1kMilkFoodProductFoodProductFoodProductFoodProductFoodProductFoodProductFoodProduct(CR)4041424344454647484950>>51't5253SunsetBayShoreline (NA)NMPSiteDischarge Area(NA)NMPSiteDischarge Area(NA)OswegoHarborArea(NA)MilkLocation¹50MilkLocation¹7MilkLocation¹16MilkLocation¹65ProduceLocation¹6**(Bergenstock)

(NA).ProduceLocation¹1**(Culeton)

(NA)ProduceLocation¹2**(Vitullo)

(NA)ProduceLocation¹5**(C.S.Parkhurst)

(NA)ProduceLocation¹3**(C.Narewski)

ProduceLocation¹4**(P.Parkhurst)

(NA)ProduceLocation¹7**(McHillen)(NA)1.5mi880'0.3mi9315'Nand/or0.6mi855'E6.2mi8235'H8.2mi993'5.5mi8107'SE5.9mi8190'17.0mi8220'H1.9mi8141'E1.7mi896'1.9mi9101'1.5mi8114'SE1.6mi884'2.1mi9110'SE15.0mi8223SN Fb NineMilePointNuclearStationRadiological Environmental Monitoring ProgramSamplingLocations Table5.1(Continued)

TypeofSamle*MapLocation(Env.Collection SiteProramNo.)LocationFoodProduct(CR)FoodProductFoodProductFoodProductFoodProduct5556575859ProduceLocation¹8**(Denman)(NA)ProduceLocation¹9*'O'onnor)

(NA)ProduceLocation¹10**(C.Lawton)(NA)ProduceLocation¹11**(C.R.Parkhurst)

(NA)ProduceLocation¹12**(Johnson)

(NA)12.6mi9225'W1.6mi8171'2.2mi8123ESE2.0mi8112'SE1.9mi8103ESEFoodProduct(CR)60"ProduceLocation¹13**(Flack)(NA)15.6mi8225'WFoodProduct61ProduceLocation¹14*'Dickenson)

(NA)1.7mi882'FoodProduct62ProduceLocation¹15**(Whaley)(NA)1.7mi9136'E*Map-SeeFigures5.1-1and5.1-2**FoodProductSamplesneednotnecessarily becollected fromalllistedlocations.

Collected sampleswillbeofthehighestcalculated siteaverageD/Q.(N/A)notapplicable CRControlResult(location) t)yII=-E%,$,144=N~~rgkq1hf t~Wy~y<a%~P~~(AI0N1012161616LAK6OHAR.gk6(CTOWER)/05(l)W,ll~IIICwnasweel 5eeyloLecetNA5W-~c(h9-~~160+tsaaolapisIroa%nFIGURE5.I-INineMllePointOn-SiteNeppch3III%I~II%%~~~PINoE'052294

('Il0pl0 Pageof2cso~aFIGURE5.I"2NINEMiLEPOINTOFF-SITEMAP(Ii88)s5*NDYCaE~nnOODCskloocnocoowocosI.EQEIIDUOOossseNylasae

...,....~j Teranesaa.cooovassocones...nsoseeasEnslconosoncol Sosnol~LocoilonLAICEONTARIO~~OasesbeniCs~s~assaaOssOssasSolessSsalsaC~sssassNs~eaersCassss*I.OI/ssrSeasIX~r!~i'CalgC~E4'oI-.JlICssarO~~OSl~sIic5wa,ISeasoVEHa)s\NoslsoqXIc.W~...scalesssosss~ph IIE,I'w!s-'r)g'@jan' osqcj~~scavsNIsMkeXIioC~0II~sI/aloesee<<~sw~sole~<<sso0oolwss<<ae4"Sess'CocossI4Pelea144P~RIasseo4ARM~4sNvIoas<<~444ssNNIRAlRAH4~Ceatral~aeasesIloessRooC0HseeeeareSSaaSaCOlaeH~eao~eae4~4~W~~'ITFeaoaeeaeaso444aseaa0easeoeeoc~e<<e44a~IDFigure5.i-2Pape2of2

-r APPENDIXALIQUIDDOSEFACTORDERIVATION 97 1l"IP"==+**4QVfply AppendixALiquidEffluentDoseFactorDerivation, AiatAiat(mrem/hrperuCi/ml)whichembodiesthedoseconversion factors,pathwaytransferfactors(e.g.,bioaccumulation factors),

pathwayusagefactors,'anddilutionfactorsforthepointsofpathwayorigintakesintoaccountthedosefromingestion offishanddrinkingwater.Thetotalbodyandorgandoseconversion factorsforeachradionuclide willbeusedfromTableE-11ofRegulatory Guide1.109.Toexpeditetime,thedoseiscalculated foramaximumindividual insteadofeachagegroup.Themaximumindividual dosefactorisacomposite ofthehighestdosefactor,Aiat,of'achagegroupa,organtandnuclidei,henceAit.Theequationforcalculating dosecontributions giveninSection,2.3requirestheuseofthecomposite dosefactorAitforeachnuclide,i.Itshouldbenotedthatthefishingestion pathwayisthemostsignificant pathwayfordosefrom,liquideffluents.

Thewaterconsumption andtheexternal'sediment exposurepathwaysareincluded-for consistency withUnit1technical specifications.

Thedosefactorequationforafreshwatersiteis:AiatKo(Uw(e-iPw)+UfBFi(eiPf)](DFL)iat

+Dwtgt..:+69.3UsWe~iPs(1-e-ib)(DFS)i(Ds)(gi).Hhere:AiatKoUwUfUs(DFL)iat(DFS)iDwDsIsthedosefactorfornuclidei,agegroupa,totalbodyororgant,forallappropriate

pathways, (mrem/hrperuCi/ml)Istheunitconversion factor,1.14E51E6pCi/uCi x1E3ml/kg-:-8760hr/yrHaterconsumption (1/yr);fromTableE-5ofReg.Guide1.109Fishconsumption (Kg/yr);fromTableE-5ofReg.Guide1.109SedimentShoreline Usage(hr/yr);fromTableE-5ofReg.Guide1.109Bioaccumulation factorfornuclide,i,infish,(pCi/kgperpCi/1),fromTableA-1ofReg.Guide1.109Doseconversion factorfornuclide,i,agegroupa,totalbodyororgant,(mrem/pCi);

fromTableE-llofReg.Guide1.109Doseconversion factorfornuclideiandtotalbody,fromstandingoncontaminated ground(mrem/hrperpCi/m2);fromTableE-6ofReg.Guide1.109Dilutionfactorfromthenearfieldareawithinone-quarter mileofthereleasepointtothepotablewaterintakefortheadultwaterconsumption.

ThisistheMetropolitan HaterBoard,OnondagaCountyintakestructure locatedwestoftheCityofOswego.(Unitless)

Di.lution factorfromthenearfieldareawithinonequartermileofthereleasepointtotheshoreline deposit(takenatthesamepointwherewetakeenvironmental samples1.5miles;unitless) 98 4%4ko~.vl,7pa":eII~

AppendixA(Cont'd)tpwtpfortpstbAveragetransittimerequiredforeachnuclidetoreachthepointof'exposure forinternaldose,itisthetotaltimeel,apsedfromreleaseofthenuclidestoeitheringestion forwater(w)andfish(f)orshoreline deposit'(s),(hr)Lengthoftimethesedimentisexposedtothecontaminated water,nominally 15yrs(approximate midpointoffacilityoperating life),(hrs).decayconstantfornuclidei(hr-1)Shore'width factor(unitless) fromTable1-2ofReg.Guide1.109ExampleCa1cu1ationForI-131ThyroidDoseFactorforanAdultfromaRadwasteliquideffluents exposure:

(OFS)i2.80E-9mrem/hrperpCi/m2(DFL)iat1.95E-3mrem/pCitpw30hrs.(wwater)BFi15pCi/KgperpCi/1tpf24hrs.(ffish)Uf21Kg/yrtb1.314E5hr(5.48E3days)Ow40unitlessUw7301/yrDs12unitlessKo1.14E5(Ci/uCi)(ml/k

)Us12hr/yr(hr/yr)N~.3~i.361E-3hr-1 tps5.5hrs(sShoreline Sediment)

ThesevalueswillyieldanAiatFactorof6.79E4mrem-mlperuCi-hraslistedinTable2-4.ItshouldbenotedthatonlyalimitednumberofnuclidesarelistedonTables2-1to2-8.Thesearethemostcommonnuclidesencountered ineffluents.

Ifanuclideis.detectedforwhichafactorisnotlisted,thenitwillbecalculated andincludhdinarevisiontotheODCH.Inaddition, notalldosefactorsforeachagegroupareusedforthedosecalculations..

Amaximumindividual isused,whichisacomposite ofthemaximumdosefactor"'of eachageg'oupforeachorganasreflected intheapplicable chemistry procedures.

99 0

APPENDIX8PLUMESHINEDOSEFACTORDERIVATION 100 X,tl"n+44.J+"

APPENDIXBForelevatedreleasestheplumeshinedosefactorsforgammaair(Bi)andwholebody(Vi),arecalculated usingthefiniteplumemodelwithanelevation abovegroundequaltothestackheight.Tocalculate theplumeshinefactorforgammawholebodydoses,thegammaairdosefactorisad)ustedfortheattenuation oftissue,andtheratioofmassabsorption coefficients betweentissueandair.Theequations areasfollows:GammaAirsl-$<ua<lasR8Vs~WholeHodVi1.11SFBie-uatd where:K*conversion factor(seebelowforactualvalue).tdtissuedepth(g/cm2)uaenergyabsorption coefficient (cm-i;airforBi,tissueforVi)EEnergyofgammarayperdisintegration (Mev)Vsaveragewindspeedforeachstability class(s),m/seR'ownwind di,stance (siteboundary, m)sectorwidth(radians)

SFshielding factorfromstructures (unitless) ssubscript forstability classIsIfunctionIl+kI2foreachstab)lity class.(unitless, seeRegulatory Guide1.109)Fractionoftheattenuated energythatisactuallyabsorbedinair(seeRegulatory Guide1.109,seebelowforequation)

Ratioofmassabsorption coefficients betweentissueandair.l1.6E-6~erMev00~erg-ragdKconversion factor3.7E10disCi-s293gI*m/3.46k~u-uauawhere:uenergyattenuation coefficient (cm-1;airforBi,tissueforVi)101 "2j APPENDIX8(Cont'd)Therearesevenstability classes,AthruF.Thepercentage oftheyearthateachstability classoccursistakenfromtheU-2FSAR.Fromthisdata,aplumeshinedosefactoriscalculated foreachstability classandeachnuclide,multiplied byitsrespective fractionandthensummed.Thewindspeedscorresponding toeachstability classare,also,takenfromtheU-2FSAR.Toconfirmtheaccuracyofthesevalues,anaverageofthe12monthwindspeedsfor1985,1986,1987and1988wascomparedtotheaverageoftheFSARvalues.Theaveragewindspeedoftheactualdata.isequalto6.78m/s,whichcomparedfavorably totheFSARaveragewindspeedequalto6.77m/s.,Theaveragegammaenergieswerecalculated usingaweightedaverageofallgammaenergiesemittedfromthenuclide.Theseenergiesweretaken"fromthe handbook"Radioactive DecayDataTables",DavidC.Kocher.Theseenergiescomparedfavorably tothosegiveninTable1-1.Theabsorption (ua)andattenuation (u)coefficients werecalculated bymultiplying themassabsorption (ua/g)andmassattenuation (u/P)coefficients givenintheRadiation HealthHandbookbytheairdensityequalto1~293E-3g/ccorthetissuedensityof1g/ccwhereapplicable.

Thedownwinddistanceisthesiteboundary.

102 5i'~OLid' APPENDIXB(Cont'd)SAMPLECALCULATION Ex.Kr-89FSTABILITY CLASSONLY-GammaAir-DATAEuaaUe-o~~k~u-ua~.871uaR~644mk.46Vf5.55m/sec2.222.943E-3m-15.5064E-3m-l

.3919m.......vertical plumespreadtakenfrom"Introduction toNuclear,Engineering",

JohnR.LaMarsh-IFunctionU~-.06I1.33I2~.45I~Il+kI2~.33+(.871)(.45)~.72~ersBi0.46(Ci-sec)(Mev

)(2.943E-3m-l)(2.22(Mev))(.72)

(g/m)(~ers)(5.55m/s)(.39)(644m)(g-rad)1.55(-6)rad/s(3600s/hr)(24h/d)(365d/)(lE3mrad/rad)

Ci/s(1E6uCi)Ci2.50(-2)~mrad/ruCi/sec103 5'c APPENDIXCDOSEPARAMETERS FORIODINE131and133,PARTICULATES ANDTRITIUM104 p"'aeWVIIQ:VIT"I~P+1Ia<<,b,y,"

APPENDIXCDOSEPARAHETERS FORIODINE-131AND-133,PARTICULATES ANDTRITIUHThisappendixcontainsthemethodology whichwasusedtocalculate theorgandosefactorsforI-131,I-133,particulates, andtritium.Thedosefactor,Ri,wascalculated usingthemethodology outlinedinNUREG-0133.

Theradioiodine andparticulate Technical Specification (Section3.6.15)isapplicable tothelocationintheunrestricted areawherethecombination ofexistingpathwaysandreceptoragegroupsindicates themaximumpotential exposureoccurs,i.e.,thecriticalreceptor.

Theinhalation andgroundplaneexposurepathwaysareconsidered to.exist atalllocations butthelandsiteboundarycriticallocationwillbeusedfordosepurposes.

Thegrass-goat-milk, thegrass-cow-milk, grass-cow-meat, andvegetation pathwaysareconsidered toexistatcriticalspecificlocations.

Hashoutwascalculated anddetermined tobenegligible.

Rivalueshavebeencalculated

'~for,the-adult;,teen, childandinfantagegroupsforallpathways.

Themethodology usedtocalculate thesevaluesfollows:A.lInhalation PathwaRi(I)where:~K(BR)a(DFA)iat Ri(I)(BR)a(DFA)iatdosefactorforeachidentified radionuclide ioftheorganofinterest(unitsmrem/hrperuCi/m3);aconstantofunitconversion, lE6pCi/uCiBreathing rateofthereceptorofagegroupa,(unitsm3/yr);Theinhalation dosefactorfornuclideiagegroupa,andtotalbodyororgant(unitsmrem/pCi).

105 Vl'UC$10 APPENDIXC(Cont'd)Thebreathing rates(BR)aforthevariousagegroups,asgiveninTableE-5ofRegulatory Guide1.109Revision1,aretabulated below.AeGrou(a)InfantBreathinRate(m3~/r)1400Chi1d3700Teen8000Adult8000Inhalation dosefactors(DFAi)aforthevariousagegroupsaregiveninTablesE-7throughE-10ofRegulatory Guide1.109Revision1.A.2GroundPlanePathwa-jiltRi(G)K'K(SF)(DFG)i (1-e)where:Ri(G)dosefactorforthegroundplanepathwayforeachidentified radionuclide ifortheorganofinterest(units-m2-mrem/yr peruCi/sec)K'lIaconstantofunitconversion, 1E6pCi/uCi;aconstantofunitconversion, 8760hr/year;ittheradiological decayconstantforradionuclide i,(unitssec-1)li,"theexposuretime,sec,4.73EBsec(1Syears);(DFG)ithegroundplanedoseconversion factorforradionuclide i(unitsmrem/hrperpCi/m2)SFtheshielding factor(dimensionless);

106 JgigaN,(4si,wr+lcrc~~wi~:a.st444 APPENDIXC(Cont'd)Ashielding factorof0.7isdiscussed inTableE-15ofRegulatory Guide1.109Revision1.Atabulation ofOFGivaluesispresented inTableE-6ofRegulatory Guide1.109Revisionl.A.3Grass-(Cow orGoat)-Milk PathwaR<<C)K'()f~<U<)>Fe(r)(DFL)le fpfe+<)gaffe)e-

<theltf<>~+qw)i"Iwhere:Ri<C)K'fUapYpYse"(OFL)iatthdosefactorfor"thecowmilkorgoatmilk.pathway, for=each-identified radionuclide ifortheorganofinterest, (units-m2-mrem/yr peruCi/sec)aconstantofunitconversion, 1E6pCi/uCi;Thecow'sorgoat'sfeedconsumption rate,(unitsKg/day-wet weight)thereceptor's milkconsumption rateforagegroupa,(units-liters/yr);

'heagricultural productivity byunitareaofpasturefeedgrass,(unitskg/m2);theagricultural productivity byunitareaofstoredfeed,(unitskg/m2)thestableelementtransfercoefficients, (unitspCi/liter perpCi/day);

fractionofdeposited activityretainedoncow'sfeedgrass;theingestion dosefactorfornuclidei,agegroupa,andtotalbodyororgant(unitsmrem/pCi);

'theradiological'ecay constantforradionuclide i,(unitssec-1);thedecayconstantforremovalofactivityonleafandplantsurfacesbyweathering equalto5.73E-7sec-1(corresponding to,a14dayha1f-1ife);th'etransport timefrompasturetocoworgoat,tomilk,toreceptor, (unitssec);thetransport timefrompasture,toharvest,tocoworgoat,tomilk,toreceptor(unitssec);107 I'a>fig$p~kII'l'.M>1+'ttf APPENDIXC(Cont'd)fpfractionoftheyearthatthecoworgoatisonpasture(dimensionless);

fsfractionofthecowfeedthatispasturegrasswhilethecowisonpasture(dimensionless);

Milkcattleandgoatsareconsidered tobefedfromtwopotential sources,pasturegrassandstoredfeeds.Following thedevelopment inRegulatory Guide1.109Revision1,thevalueoffsisconsidered unityinlieuofsitespecificinformation.

Thevalueoffpis0.5basedon6monthgrazingperiod.Thisvalueforfpwasobtainedfromtheenvironmental group.TableC-1containstheappropriate valuesandtheirsource,in Regulatory Guide1.109Revisionl.Theconcentration oftritiuminmilkisbasedontheairborneconcentration ratherthanthedeposition.

Therefore, theRT(C)isbasedonX/Q:RT(C)~K'KmQfUap(DFL)iat 0.75(0.5/H)

'where:RT(C)dosefactorforthecoworgoatmilkpathway.fortritiumfortheorganofinterest, (unitsmrem/yrperuCi/m3);Kaconstantofunitconversion, lE3g/kg;H-'bsolutehumidityoftheatmosphere, (unitsg/m3);0.75thefractionoftotalfeedthatiswater;0.5therati'oofthespecificactivityofthefeedgrasswatertotheatmospheric water.Othervaluesaregivenpreviously.

AsitespecificvalueofHequalto6.14g/m3isused.Thisvaluewasobtainedfromtheenvironmental group"usingactual'site data.108 h'IfI'L1',1,'I'>TV+~IV,4i/I<<AVHl-WfI~'IQ'IIV APPENDIXC(Cont'd)A.4Grass-Cow-Meat PathwaRi(H)~K'QfUapFf(r)(DFL)iat (s~+~)-4tf5ff(1-ff)ep+eRi(H)dosefactorforthemeatingestion pathwayforradionuclide iforanyorganofinterest, (unitsm~-mrem/yr peruCi/sec);

Ffthestableelementtransfercoefficients, (unitsdays/Kg);

Uapthereceptor's meatconsumption rateforagegroupa,(unitskg/year);

ththetransport timefromharvest,tocow,toreceptor, (unitssec)tfthetransport timefrompasture,tocow,toreceptor, (unitssec)Allothertermsremainthesameasdefinedforthemilkpathway.TableC-2containsthevalueswhichwereusedincalculating Ri(H).Theconcentration oftritiuminmeatisbased"onairborneconcentration ratherthan'deposition.

Therefore, theRT(H)isbasedonX/Q.RT(H)~KKFfQfUap(DFL) iatk075(0~5/H))where:RT(M)dosefactorforthemeatingestion pathwayfortritiumforanyorganofinterest, (unitsmrem/yrperuCi/m3).Allothertermsaredefinedabove.A.SVeetationPathwa"'.'",'"'The"i'n'tegrated'concentration invegetation consumedbymanfollowstheexpression developed formilk.Hanisconsidered toconsumetwotypesofvegetation (freshandstored)thatdifferonlyinthetimeperiodbetweenharvestand,consumption, therefore:

.'Ri(V)K'v(ki+Xw)

(DFL)iatUL)aFLe+US)aFge109 (kwlw31)

APPENDIXC(Cont'd)where:Ri.<V)dosefactorforvegetable pathwayforradionuclide ifortheorganofinterest, (unitsm~-mrem/yr peruCi/sec);

K'L)Us)thaconstantofunitconversion, lE6pCi/uCi;theconsumption rateoffreshleafyvegetation bythereceptorinagegroupa,(unitskg/yr);theconsumption rateofstoredvegetation bythereceptorinagegroupa(unitskg/yr).thefractionoftheannualintakeoffreshleafyvegetation grownlocally;thefractionoftheannualintakeofstoredvegetation grownlocally;theaveragetimebetweenharvestofleafyvegetation anditsconsumption, (unitssec);theaveragetimebetweenharvestofstoredvegetation anditsconsumption, (units-sec);Yv*thevegetation areadensity,<unitskg/m~);Allotherfactorsaredefinedpreviously.

TableC-3presentstheappropriate parameter valuesandtheirsourceinRegulatory Guide1.109Revision1.Inlieuofsite-specific data,valuesforfLandfgof,1.0and0.76,respectively, wereusedinthecalculation.

ThesevalueswereobtainedfromTableE-15ofRegulatory Guide1.109Revisionl.110

'kg*II APPENDIXC(Cont'd)Theconcentration oftritiuminvegetation isbasedontheairborneconcentration ratherthanthedeposition.

Therefore, theRT(V)isbasedonX/Q:RT(V)~K'K")fL+Us)afDFL)iat0.75(0.5/H) where:RT(V)dosefactorforthevegetable pathwayfortritiumforanyorganofinterest, (unitsmrem/yrperuCi/m3).Allothertermsaredefinedinpreceeding sections.

Pjg1'VV TABLEC-1Parameters forGrass-(Cow orGoat)-HilkPathwaysParameter Qf(kg/day)(OFL)iat(mrem/pCi)

Fm(pCi/liter perpCi/day)Ys(kg/m2)Yp(kg/m2)'h(seconds) tf(seconds)

Uap(liters/yr)

Value50(cow)6(goat)1.0(radioiodines) 0.2(particulates)

Eachradionuclide Eachstableelement2.00.7778x106(90days)1.73x105(2days)330infant330child400teen310adultReference (Re.Guide1.109Rev.1)TableE-3TableE-3TableE-15TableE-15TablesE-11toE-14TableE-1(cow)TableE-2(goat)TableE-15TableE-15TableE-15TableE-15TableE-5TableE-5TableE-5TableE-5112 07~Fh'l'hf'.

TABLEC-2Parameters fortheGrass-Cow-Heat PathwayParameter ff(pCi/KgperpCi/day)"ap(Kg/yr)<DFL)iat(mrem/pCi)

Yp(kg/m)Ys<kg/m2)th(seconds) tf(seconds)

Qf(kg/day)Value1.0<radioiodines) 0.2(particulates)

Eachstableelement0infant41child65teen110adultEachradionuclide 0.72.07.78E6(90days)1.73E6(20days)50Reference (Re.Guide1.109Rev.1)TableE-15TableE-15TableE-1TableE-5TableE-5TableE-5TableE-5TablesE-lltoE-14TableE-15TableE-15TableE-15TableE-15TableE-3113

~ACAfi/'1 TABLEC-3Parameters fortheVegetable PathwayParameter r(dimensionless)

.Value1.0(radioiodines) 0.2(particulates)

Reference (Re.Guide1.109Rev.1)TableE-1TableE-1(DFL)iat(mrem/pCi

)UL)(kg/yr)-infant-child-teen-adultEach"radionuclide 0264264TablesTableTableTableTableE-11toE-14E-5E-5E-5E-5Us)a(kg/yr)-infant-child-teen-adulttL.(seconds) th(seconds)

Yv(kg/m2)05206305208.6E4(1day)5.18E6(60days)2.0TableE-5TableE-5TableE-5TableE-5TableE-15TableE-15TableE-15114 r'I(e APPENDIXDDIAGRAMSOFLIQUIDANDGASEOUSRADWASTETREATMENT SYSTEMS115 A*~~rP's,ll~~-t14g,g'-1~eA-I E~0<<elle>I~<<Psaa<<>leKvvecCKICKtnISCl~I~0NCI~II>>'rs~NI0N~~t<<lllho~IWSIhs~Ic~N~1~I~~CKtIc~~0~I~I~1lc~I~ItlN~><<<<IIIWtN<<Ill~h>>No<<sC~II~IPIPINCtINSTRUHENT ANOEOUIPHENT SYHBOLSN~0I~K'<<NIN~K'~I~tl~N~N~as~~>I~INossa!ul~NWho~~~14Ilarl~s~1~0Nt!sh(Sstsisaftva-a=.'<<laVvalth>>>>I<<lo~VII<<la1stl<<laF<<Iheh<<o~wwog0Ihase<<o~>>Nswa~<<II~IhK>NI~<<ll<<as,I~hhsa>Lt>>II>>aol>>s~aoI<<<<Ulseastpts<<atj)thh>WSh>to>>soaro<<K.LIIILSTI!II!L'K ta<<roIlpho>oarsIo>>wp>>Nteal>1<<0~<<l>>collw<<aIos~C<<>>I0lolls~ol<<0a<>ccsrh<<IlccC>>CII>0CW>40~~P>><<tl~I<<Is>>~>>>lalh>>IS<<CIO>>Clo>01>>I8)..Q)-Plo<<KNo<<ss>>Nh~l'II'II-IKI<<0hw&s>>Q0<<~04l~<<col>>>>os>>ewos

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~TIOOM~I,AHCLCV+TlON CRAPNICISaIIINCTICrIIaaCpLiTsaaIIhATsaaNCIVIC,CIIVceea A.J504'TD CLTSaIs~assassUNCS~PAM~.cavo~SlJkRIsT'IR'SIsTOraSOIOVAT(ONLOOKINONORTH-121-FIGURED-5SI1StackNIAGARAMOHAWKPOWERCORPORATION NINEMILEPOINTUNITjOFFIITRDOIlfCALCMANUAL 4fkilIbI*t OFFCASBUILOINCVENTILATION SYSTEMwla~awwa)~a44~AAII'Da~laaaaaaaata~wa4Ka'v~aaNjtwaafsw~WaafKllL'"AAII~W4aaaIIaaAAAIKAa44aaO~AatV~I+W5Jaa'V~wat~DCa'VItlItI-~FCUREOffGASBUIIDIBGVfllllIAIIOII SYSllNWAawwawawlaaWa~altaI'IIAOAA*

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-NMP2ReactorBuildingVentislocated187feetabovegroundlevel-JAFNPPReactorandTurbineBuildingVentsarelocated173feetabovegroundlevel-JAFNPPRadwasteBuildingVentis112feetabovegroundlevel-TheEnergyInformation Centerandadjoining picnicareaareUNRESTRICTED

'-.-"".AREAS:.wi.thin, theSITEBOUNDARYthatareaccessible toMEMBERSOFTHEPUBLIC-LakeRoad,aprivateroad,isanUNRESTRICTED AREAwithintheSITEBOUNDARYaccessible toMEMBERSOFTHEPUBLIC-l24-0'*~a,sac,rNV4r41%

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&Ew'4Iilla~otalCV'IIO ISOKINETIC PROBERN2111241RAGEMSRAGEMSDitutionReturn112-52112-131]SampleReturnDrain112-5511243112-132112.57OGESMSIntet112.30112-56112-133OGESMSOuttetFigureD-9StackSampleandSampleReturnNIAGARAMOHAWKPOWERCORPORATION NINEMILEPOINT-UNIT1OFFSlTEDOSECALC.MANUAL126-SlitF'~~Jtel RAGEMSinletOVS112-173OV3112-169OV2112-167PCV112-106112-110NeSupplyOV8112-17812-1Pl112-21OV4112-171OFS1112-101AC112.130112-51OV1OV13112-165t1248RAGEMSDilutionInletOFC4112-104OFS4112-04APCV112-107OFC1112-101112-111Pl11-122OFC3112-103OFS3112-103A112-116OCF2112-102OFS2112-102A112-151OV16112-150112-112Pl"11-23OV12Senlpte112+7ReturnRAGEMSOutlet112-113Pl112-24112-117112-118OP2OP1OV6112-175Figure0-1011-44RAGEMSDilutionSchematic NIAGARAMOHAWKPOWERCORPORATION NINEMlLEPOINT-UNIT1OFFSITEDOSECALC.MANUAL127 IP'~)~ir14glg 112-1141FS1112-129Pl112-1251V31V4112-183112-185,'V3 2V4112-199112-2013V3112.73V16112-2183V112-96Qalhn2Tritium112-73112-72112-743FS1112-105A1V1112-11V212-'I812VI112-1952112-1973VI3VS112332.776Uter-95112-99.75Pl112-1263GVI112-1051V5112-1861V62VS112-187112-2022V6112-2032V11112-2081176I-78333V4112.98112-1193V63V7112-100112-211Pl112471V11112-192Pl112441V17112493V11112-2153VI112-217'l12-1083PI3VIO112-21I3VI2112-109112-216FiUreD-11RAGEMSSchematic NIAGARAMOHAWKPOWERCORPORATION NINEMILEPOINT-UNIT1OFFSITEDOSECALC.MANUAL128 P+A.JatAt'a'~<<a1 011242FS1143112-1011249AM43A6711266112-11Inlet112-146112-147112-59FL1112-58112-14812-1491126111240u112-137112-152Pl112-uu1126263112-153BA-G-3112-154'l124411245uu112-1611124811244FGV112-91112-137112-163112-134BRG-3PS2114i11-1351'l2-135112-139112-138112-140FS112-94Fl11246TritiumV/Pl1124512-158q112-156112-155112-142l12-141112-22FL3112-20112.2111240112-159112-'157112-3112-19112-112112.14112.1811249112-70112-1512-1112-121124711248FiureD-12OGESMSSchematic NIAGARAMOHAWKPOWERCORPORATION NINEMILEPOINT-UNIT1OFFSITEDOSECALC.MANUAL129-

'1yl,llif~8J ANMPITNSUPERSKOEQ Ol4REPLICAGeneralSuperintendent NuclearGeneration K.A.DahlbergforL.Will1s311,2,5,6,8,9,11-13,15-18, 36-44,47-49, 52-63,65-76,79-81,86-116 3,4,7,10,14,20,23 27-28,30-35 45,46,50,51,82-85

  • 29*64,77,78 i,19,21,22A,22B,24,25 26,112February1987December1987January1988May1988(Reissue)

May27,1988(Reissue)

February1990THISPROCEDURE NOTTOBEUSEDAFTERMarch1992SUBJECTTOPERIODICREVIEW9PP9110036 e.~lV 1.02.02~1INTRODUCTION LIQUIDEFFLUENTS SetpointDeterminations 2.1.1Basis2.1.2ServiceWaterSystemEffluentAlarmSetpoint2.1.32.1.4LiquidRadwasteEffluentAlarmSetpointDiscussion 2.1.4.1ControlofLiquidEffluentBatchDischarges 2.1.4.2Simultaneous Discharges ofRadioactive Liquids2.1.4.3SampleRepresentativeness 2.1.4.4LiquidRadwasteSystemOperation 2.1.4.52.22.32.3.1;3.03.13.1.13.1.23.1.'33.1.43.1.53.1.5.13.1.5.2ServiceWaterSystemContamination LiquidEffluentConcentration Calculation DoseDeterminations MaximumDoseEquivalent Pathway"-GASEOUS EFFLUENTS SetpointDeterminations BasisStackMonitorSetpoints Recombiner Discharge-(Off Gas)MonitorSetpoints Emergency Condenser VentMonitorSetpointDiscussion StackEffluentMonitoring SystemDescription StackSampleFlowPath-RAGEHS1012121919192022BI~'324243.1.5.3StackSampleFlowPath-OGESHS26

/jW'-74vv~,lklr~P~Ih4".II<OA TABFT(Cont'd)3,1.5.4SampleFrequency/Sample Analysis3.1.5.5I-133Estimates 3.1.5.6GaseousRadwasteTreatment SystemOperation 2727,283.23.2.1DoseandDose.RateDetermination DoseRate29313.2.1.1NobleGases3.2.1.2Tritium,IodinesandParticulates

'3.'2.2Dose3.2.2.1NobleGasAirDose3.2.2.2Radioiodine, TritiumandParticulates 3.2.2.3Accumulating Doses3.3-"CriticalReceptors 323234343637383.44.04.14.24.3'.45.05.15.25.3Refinement ofOffsiteDosesResulting FromEmergency Condenser VentReleases40CFR190REQUIREMENTS

-:Evaluations ofDosesFromLiquidEffluents Evaluation ofDosesFromGaseousEffluents Evaluation ofDosesFromDirectRadiation DosestoMembersof,thePublicHithintheSiteBoundaryENVIRONMENTAL MONITORING PROGRAMSamplingStationsInterlaboratory Comparison ProgramCapabilities for'Thermoluminescent Dosimeters UsedforEnvironmental Measurements.

3940'64647525354

'll,F ODCM-NINEMILEPOINTMILE1TABLEOFCONTENTS(Cont'd)~PaeTable1-1Table1-2Table2-1Table3-1Rapj1Values.fortheNMP-1FacilityParameters fortheLiquidEffluentPathwayAverageEnergyPerDisintegration CriticalReceptorDispersion Parameters forGroundLevelandElevatedReleases57585960Table4-1DoseFactorsforNobleGases61-Tables4-2to4-20RValues62Table5-1NMP-1Radiological Environmental Monitoring ProgremSamplingLocations 81AppendixADoseParameters forIodine-131and133,Particulates andTritium85AppendixBDiagramsofLiquidsandGaseousRadwasteTreatments Systems98AppendixCDispersion Calculation Tables109

~/~hppV44c~

1o0INTRODUCTION TheOffsiteDoseCalculation Manual(ODCM)providesthemethodology tobeusedfordemonstrating compliance"with theRadiological EffluentTechnical Specifications (RETS),10CFR20,10CFR50,and40CFR190'hecontentsoftheODCMarebasedonDraftNUREG-0472, Revision3,"Standard Radiological EffluentTechnical Specifications forPressurized Water'eactors,"

September 1982;DraftNUREG-0473, Revision2,-"Radiological

.EffluentTechnical S'pecifications forBWR's,"July1979;NUREG0133,"Preparation ofRadiological EffluentTechnical Specifications forNuclearPowerPlants,"October1978;theseveralRegulatory Guidesreferenced inthesedocuments; and,communication withtheNRCstaff.Section5containsadetaileddescription oftheRadiological Environmental Monitoring (REM)samplinglocations'hould itbenecessary torevisetheODCM,theserevisions willbemadeinaccordance withTechnical Specifications i5iI~fr'4a)

2.0 LIQUIDEFFLUENTS

2.1SetpointDeterminations 2.1.1BasisMonitorsetpoints willbeestablished suchthattheconcentration ofradionuclides intheliquideffluentreleasesinthedischarge canalwillnotexceedthoseconcentrations asspecified in10CFR20,AppendixB,TableII,Column2.Setpoints fortheServiceWaterSystemEffluentLinewillbecalculated'uarterly basedontheradionuclides identified duringthepreviousyear'sreleasesfromtheliquidradwastesystemortheisotopesidentified inthemostrecentradwastereleaseorotheridentified probablesource.Setpoints fortheLiquidRadwasteEffluentLinewillbebasedontheradionuclides identified ineachbatchofliquidwastepriortoitsrelease.tlAfterrelease,theLiquidRadwastemonitorsetpointmayremainasset,orrevertbacktoasetpointbasedonapreviousSemi-Annual Radioactive EffluentReleaseReport,orinstallblankflangeinthedischarge lineanddeclareinoperable inaccordance.

withthetechnical specification.

SincetheServiceWaterSystemeffluentmonitorandLiquidRadwasteeffluentmonitorcanonlydetectgammaradiation, thealarmsetpoints arecalculated by-usingtheconcentration ofgammaemittingisotopesonly(orthecorresponding MPCvaluesforthesameisotopes, whichever arehigher)E(Ci/ml)expression (Section2.1.2,2.1.3).-2-inthe Pf1I8~-'f4K 2.1.1(Cont'd)TheRequiredDilutionFactoriscalculated usingconcentrations ofallisotopespresent(orthecorresponding MPCvaluesforthesameisotopes, whichever arehigher)including tritiumandothernon-gamma emitterstoensurethatallradionuclides inthedischarge canaldonotexceed10CFR20limits.2.1.2ServiceWaterSystemEffluentLineAlarmSetpointThedetailedmethodsforestablishing setpoints fortheServiceWaterSystemEffluentLineMonitorshallbecontained intheNineMilePointStationProcedures.

Thesemethodsshallbeinaccordance withthefollowing:

+background (5(liCi/ml)i

~concentration ofgammaemittingisotopeiinthesample,orthecorresponding MPCofgammaemittingisotopei'MPC)i',whichever ishigher(units~uCi/ml)-(vCi/ml)iT

~concentration ofanyradioactive isotopeiinthesampleincluding tritiumandothernon-gamma emittersorcorresponding MPCofisotopei,MPCi,whichever is.higher(units~vCi/ml).Setpoint(Hialarm)<0.9 z(nCi/ml)i CF)TDF/Fswbackground

/Setpoint(Alertalarm)<0.7 E(pCi/ml)i (CF)TDF/FswEf(pCi/ml)jT/MPCiJ-TotalDilutionFlow(unitsgallons/min)

FswServiceWaterFlow(unitsgallons/min)

CF~monitorcalibration factor(units~netcpm/uCi/ml)

MPCiliquideffluentradioactivity concentrations limitforradionuclide iasspecified in10CFR20,AppendixB,TableII,Column2.

gJ'V-'lka~'QW.Pllsling~tgkrq4/5

~~~2.1.2Sample(VpC)iO.aand0.7(Cont'd)ThosenuclidespresentinthepreviousbatchreleasefromtheliquidradwasteeffluentsystemorthosenuclidespresentinthelastSemi-annual Radioactive EffluentReleaseReport(units~pCi/ml)orthosenuclidespresentintheservicewatersystem.**

sameasMPCibutforgammaemittingnuclidesonly.~factorsofconservatism toaccountforinaccuracies.,

Tf(uCi/ml)iT/MPCi]RequiredDilutionFactor.IfMPCvaluesareusedinthe~(uCi/ml)i, theymustalsobeusedincalculating RDF(numerator).

)sTDF/Fsw~ActualDilutionFactor*+ForperiodswithknownreactorwatertoRCLCsystemleakage,RCLCmaximumpermissible concentration maybeprudently substituted fortheabove.2-1.3LiquidRadwasteEffluentLineAlarmSetpointThedetailedmethodsforestablishing setpoints fortheLiquidRadwasteEffluentLineMonitorshallbecontained in'theNineMilePointStationProcedures.

Thesemethodsshallbeinaccordance withthefollowing:

Setpoint(Hi-Hialarm)<0.9>(uCi/ml)i (CF)TDF/FxeZ[(pCi/ml)iT/MPCi]

+background Setpoint(Hialarm)<0'7(pCi/ml)i (CF)TDF/Fre+background Z[(vCi/ml)jT/MPCj](vCi/ml)i

~concentration ofgammaemittingisotopeiinthesampleor,thecorresponding MPCofgammaemittingisotopei(MPC)i~whichever ishigher.(<<Ci/ml)iT

~concentration ofanyradioactive isotopeiinthesampleincluding tritiumandothernon-gamma emittersorthecorresponding MPCofisotopeiMPCiwhichever ishigher.(units~pCi/ml)'TDF~TotalDilutionFlow(units~gallons/min)

FreCFRadwasteEffluentFlow(units~gallons/min) monitorcalibration factor(units~netcps/pCi/ml) hn44s MPCiliquideffluentradioactivity concentration limitfor'radionuclide,i asspecified in10CFR20,AppendixB,TableII,Column2,forthosenuclidesdetectedbyspectralanalysisofthecontentsoftheradwastetankstobereleased.

(units~yCi/ml)(MPC)ig~sameasMPCibutforgammaemittingnuclideonly.0.9=and0.7~factorsof.conservatism

.,to.account.forinaccuracies.

f(uCi/ml)iT/MPCij

~Required DilutionFactor.*IfMPCvaluesareusedintheE(uCi/ml) i,theymustalsobeusedincalculating RDF(numerator).

Notes:(a)

IfTDF/Fre~E[(pCi/ml)iT/MPCi]

thedischarge couldnotbemade,sincethemonitorwouldbe;continuously inalarm.Toavoidthissituation, Fwillrebereduced(normally byafactorof2)toallowsettingthealarmpointataconcentration higherthantankconcentration.

Thiswillalsoresultinadischarge canal'concentration atapproximately 50'aximum permissible concentration.

(b)ThevalueusedforTDFwillbereducedbythefractional

'uantity(1-FT),whereFTistempering fraction(i.e.,diversion ofsomefractionofdischarge flowtotheintakecanalforthepurposeoftemperature control).

$/P,q*v*4$'.gor.ka 2.1.4Discussion 2.1.4.1ControlofLiquidEffluentBatchDischarges AtNineMilePointUnit1LiquidRadwasteEffluents arereleasedonlyonabatchmode.Topreventtheinadvertent releaseofanyliquidradwasteeffluents, radwastedischarge ismechanically isolated(blankflangeinstalled ordischarge valvechain-locked closed)following thecompletion ofabatchreleaseorseriesofbatchreleases.

Thismechanical isolation remainsin.placeandwillonlyberemovedpriortothenextseriesofliquidradwastedischarges afterallanalysesrequiredinstationprocedures andTechnical Specification Table4.6.15-1A areperformed andmonitorsetpoints havebeenproperlyadjusted.

2.1.4.2Simultaneous Discharges ofRadioactive Liquids.Ifduring,thedischarge ofanyliquidradwastebatch,thereisanindication thattheservicewatercanalhasbecomecontaminated (throughaservicewatermonitoralarmorthroughagrabsampleanalysisintheeventthattheservicewatermonitor.isinoperable),

'thedischarge shallbeterminated immediately.

The'liquid radwastedischarge shallnotbecontinued untilthecauseoftheservicewateralarm(orhighgr'absampleanalysisresult)hasbeendetermined andtheappropriate corrective measurestakentoensurelOCFR20,AppendixB,TableII,Column2(Technical Specification Section3.6.15.a(1))

limitsarenotexceeded.

ir->i~+~C 2.1.4.3SamplingRepresentativeness

-ThissectioncoversTechnical Specification Table4.6.15-1Notebconcerning thoroughly mixingofeachbatchofliquidradwastepriortosampling.

LiquidRadwasteTanksscheduled fordischarge-at NineMilePointUnit1areisolated(i.e.inletvalvesmarkedup)andatleasttwotankvolumesofentrained fluidsarerecirculated priortosampling.

Minimumrecirculation timeiscalculated asfollows:'-MinimumRecirculation Time2.0(T/R)Where:2.0Plantestablished mixingfactor,unitlessTankvolume,galRecirculation flowrate,gpm.Additionally, theHiAlarmsetpointoftheLiquidRadwasteEffluentRadiation Monitorissetatavaluecorresponding tonotmorethan70Xofitscalculated responsetothegrabsampleorcorresponding MPCvalues.Thus,thisradiation monitorwillalarmifthegrabsample,orcorresponding MPCvalue,issignificantly lowerinactivitythananypartofthetankcontentsbeingdischarged.

J~,yi~,~~~~y>~Qy

~i~f-'~',"">"'~c"~~S,+i 2.1.4.4LiquidRadwasteSystemsOperation Technical Specification 3.6.16.arequiresthattheliquidradwastesystemshallbeusedtoreducetheradioactive materials inliquid~astespriortotheirdischarge, asnecessary, tomeettheconcentration anddoserequirements ofTechnical Specification 3.6.15~"Utilization oftheradwastesystemwillbebasedonthecapability oftheindicated components ofeachprocesssystemtoprocesscontentsoftherespective lowconductivity andhighconductivity collection tanks:1)LowConductivity (Equipment Drains):RadwasteFilterandRadwasteDemin.(SeeFig.B-1)2)HighConductivity (FloorDrains):WasteEvaporator (seeFig.~B-1)

"-'">>""'>'Cumulative

.dosecontributions fromliquideffluents forthecurrentcalendarquarterandthecurrentcalendaryearshallbedetermined asdescribed inSection2.3ofthismanualpriortothereleaseofeachbatchof.liquid-waste.Thissamedoseprojection ofSection2.3willalsobeperformed intheeventthatuntreated liquidwasteis=.discharged, toensurethatthedoselimitsofTechnical Specification 3.6.15.a(2) arenotexceeded.

(Therebyimplementing therequirements of10CFR50.36a, GeneralDesignCriteria60ofAppendixAandtheDesignObjective giveninSectionII-DofAppendixIto10CFR50).

1pCcI.-,"1,P4g>>$CW41~~"k,*fdic'II 2.1.4.4(Cont'd)Forthepurposeofdoseprojection, thefollowing assumptions shallbemadewithregardtoconcentrations ofnon-gamma emittingradionuclides subsequently analyzedoff-site:

a)[H-3]>H-3Concentration foundrecentcondensate storagetankanalysis.

b)[Sr-89]>4xCs-137Concentration c)[Sr-90]>0.5xCs-137Concentration d)[Fe-55]>1xCo-60Concentration AssumedScalingFactorsusedinb,c,anddabove.represent conservative estimates derivedfromanalysisofhistorical datafromprocesswastestreams.Following receiptofoff-siteH-3,Sr-89,Sr-90andFe-55analysisinformation, doseestimates shallberevisedusingactualradionuclide concentrations andactualtankvolumesdischarged.

4g!Pa 2.1.4.5ServiceWaterSystemContamination Servicewateris"normally non-radioactive.

Ifcontamination issuspected, asindicated byasfgnificant increaseinservicewatereffluentmonitorresponse, grabsampleswillbeobtainedfromtheservicewaterdischarge linesandagammaisotopicanalysismeetingtheLLDrequirements ofTechnical Specification Table4.6.15-1completed.

If'itis'determined thataninadvertent radioactive discharge isoccurring fromtheservicewatersystem,then:a)A50.59safetyevaluation shallbeperformed (ref.IGEBulletin'0-10),b)Dailyservicewatereffluentsamplesshallbetakenandanalyzedforprincipal gammaemittersuntilthereleaseisterminated, Hc)Anincidentcomposite shallbepreparedforH-3,grossalpha,Sr-89,Sr-90andFe-55analysesandd)Doseprojections shallbeperformed inaccordance withSection2.3ofthismanual(usingestimated concentrations forH-3,Sr-89,Sr-90andFe-55tobeconservatively determined by=supervision atthe.timeoftheincident).

Additionally, servicewatereffluentmonitorsetpoints mayberecalculated usingtheactualdistribution ofisotopesfoundfromsampleanalysis.

aAVCVCtlJQI 2.2LiquidEffluentConcentration Calculation Thiscalculation documents compliance withTechnical Specification Section3.6.1.5.a (1).Theconcentration ofradioactive materialreleasedinliquideffluents tounrestricted areas(seeFigureB-7)shallbelimitedto.theconcentrations specified in10CFR20,AppendixB,TableII,Column2,forradionuclides otherthandissolved orentrained noblegases.Fordissolved orentrained noblegases,theconcentration shallbelimitedto2E-4microcurie/ml totalactivity.

Theconcentration ofradioactivity fromLiquidRadwastebatchreleasesand,ifapplicable, ServiceWaterSysteminadvertent discharges areincludedinthecalculation.

Thecalculation isperformed foraspecificperiod,oftime.Nocredittakenforaveraging overthecalendaryearaspermitted by10CFR20.106.

The"limitingconcentration iscalculated asfollows:MPCFraction~E.[Z

((yCi/ml)

~F)/(MPCI(F))l1sississWhere:MPCFraction~Thelimitingconcentration of10CFR20,AppendixB,TableII,forradionuclides otherthandissolved orentrained noblegases.Fornoblegases,theconcentration shallbelimitedto28-4microcurie/ml totalactivity.

p45.i;fC4j 2.2(Cont'd)(<<Ci/ml)isFsMPCiZ((ICi/ml)

"F)sissTheconcentration ofnuclideiin.particular effluentstreams,uCi/ml.Theflowrateofaparticular effluentstreams,gpm.Thelimitingconcentration ofaspecificnuclideifrom10CFR20,Appendixb,TableII,Column2(noblegaslimitis2E-4pCi/ml)Thetotalactivityrateofnuclidei,inalleffluentstreamss,pCi/ml"gpm

~Thetotalflowrateofalleffluentstreamss,gpm(including thosestreamswhichdonotcontainradioactivity).

A.valueoflessthanoneforMPCfractionis'considered acceptable forcompliance withTechnical Specification Section3.6.15.a.(1).

2.3DoseDetermination 2.3.1MaximumDoseEquivalent Pathway.Adoseassessment reportwaspreparedfortheNineMilePointUnit1facilitybyCharlesT.Main,Inc.,ofBoston,MA.Thisreportpresented thecalculated doseequivalent ratestoindividuals aswellasthepopulation withina50~ileradiusofthefacilitybasedontheradionuclides releasedinliquidandgaseouseffluents duringthetimeperiodsof1.July1980"through31December1980and.from,.lJanuary'1981through"'31'December:1981.

Utilizing the.effluent.

data

+CDlil'w'Ifqvvg~Ayp peg~-(yis'tA8~>5',"vk 2.3.1(Cont'd)contained intheSemi-Annual Radioactive EffluentReleaseReportsassourceterms,doseequivalent ratesweredetermined usingthe'environmental pathwaymodels-specified inRegulatory Guides1.109and'.111asincorporated

-intheNRCcomputercodesLADTAPforliquidpathways, andXOQDOQand"GASPARforgaseous-effluent pathways.

Dose=.equivalent rateswere'calculated forthetotalbodyaswellassevenorgansand/ortissuesforadults,teenagers,

children, andinfants.Fromthestandpoint ofliquideffluents, thepathwaysevaluated includedfishingestion, drinkingwater,andexternalexposuretowaterandsediment.

Basedonthefindingsoftheabovereferenced report,themaximumtotal.bodydosefromallliquidpathwaysisreceivedbyanadult.Similarly, themaximumtotaldosetoanyorganisreceivedbytheteenliver.Inbothofthesecases(i.e.,adultwholebodydoseandteenliverdose),99Kand98Krespectively ofthesedoseswere"'""-~-".~"'received.via.the fishingestion pathway.Inordertodetermine thedosecontribution fromthereleaseofliquid,effluents, the'nnual dose,to.an adultwholebodyanda,teenliverwillbecalculated for"eachof,thesignificant

nuclides, (see..Table1-1)identified intheliquidwastebasedonthefishingestion pathwayutilizing thefollowing formula:R..~1100UMZB.D..(-g.t)/FapjiapPipaipjexpip yt,t'.'fjltIK WhereRtotalannualdose(perCuriereleased) toorgan"j"ofindividuals ofagegroup"a"fromallofthenuclides"i"inpathway"p"(units~mrem/year

-Ci)tJapusagefactorspecifying theexposuretimeor,intakerateforanindividual ofanagegroup"a"associated withpathway"p"(unitskg/year)mixingrates(reciprocal ofdilutionfactor)at'thepointofexposureorpointofharvest(units~dimensionless) flowrateoftheliquideffluent(unitsft/sec)3ipequilibrium bioaccumulation factorfornuclide"i"inpathway"p"'units~liters/kg)

Daipjthedosefactor,specifictoaspecificagegroup,'"a",radionuclide "i",pathway"p",andorgan"j",whichcanbeutilizedtocalculate theradiation dosefromanintakeofaradionuclide (units~mrem/pCi) radioactive decayconstantofnuclide"i"(units-1~hours) k4i'yl~r+IIcdMINIpI theaveragetransittimerequiredfornuclidestoreachthepointofexposure.

Forinternaldose,tisthetotaltimeelapsedbetweenthePreleaseofthenuclidesandtheingestion oftheEoodand/orwater(units~hours)1100~factortoconvertfrom(Ci/year)/(Et

/sec)topCi/liter 3ValuesforRiarecontained inTable1-1.AllofthesevaluesapjiofR.iareonaperCuriebasisforeachofthenuclidesapjireleased.

Table1-2indicates thoseparameters usedforselectedEactorsoftheformula.Priortoeachradioactive liquiddischarge, eachliquidwastetanktobedischarged willbeanalyzedforisotopecontentutilizing agammaspectroscopy system.Onthebasisofthisanalysis, projected doses,toanadultwholebodyandateenliverwillbecalculated usingthefollowing relationships:

PDi,1.05Rji()CiPDLi1.05Rji(L)CWherePDProjected doseexpectedtothewholebodyofanadultduetothereleaseoftheidentified concentration ofnuclide"i".(units~mrem/year)

~M'C<'QteP,ty~\0~~

PDProjected doseexpectedtotheliverofateenagerduetothereleaseoftheidentified concentration ofnuclide"i"(units~mrem/year R..(WB)apj1totalannualdose(perCuriereleased) tothewholebodyofanadultcausedbytheingestion ofnuclide"i"(units~mrem/year-Curie)

R.(L)apjitotalannualdose(perCuriereleased) totheliverofateenagercausedbytheingestion ofnuclide"i"(units.~mrem/year-Curie) cquanityofnuclide"i"identified aspresentintherelease(units~Curies)1.05~correction factortoaccountfor100%ofdose,assumingthat95%ofdosereceivedisdelivered viathefishingestion pathway.Thevalueof1.05isusedintheequationasaconservative factortoincreasetheprojected dosefromananticipated releaseto100%.Aslongasthe1.05factorisused,dosesreceivedviathedrinkingwaterpathway(eg,tritium)neednotbeaccounted forseparately.

r+IEjatl,,'i Allpro5ected dosescalculated inthismannerforeachbatchofliquideffluentwillbe'ummedforcomparison withquarterly andannuallimits,addedtothedosesaccumulated fromotherreleasesin'hequarterandyearofinterest.

Inallcases,thefollowing relationships willhold-Foracalendarquarter:D<1.5mremtotal.bodyrD<5mremforanyorgant-Forthecalendaryear:D<3.0mremtotalbody'-D<10mremforanyorganwhereDtotaldosereceivedduetoliquideffluentreleasesIftheselimitsareexceeded, aspecialreportwillbesubmitted totheNRCidentifying thecause'and proposedcorrective'actions.

Inaddition, iftheselimitsareexceededbyafactoroftwo,calculations shallbemadetodetermine ifthedoselimits-contained in"40CPR190have.beenexceeded.

Doselimits,ascontained in40CFR190aretotalbodyandorgandosesof25mremperyearandathyroiddoseof75mremperyear.

r,'IP 2.3.1(Cont'd)Thesecalculations willincludedosesasaresultofliquidandgaseouspathwaysaswellasdosesfromdirectradiation.

Liquid,gaseousanddirectradiation pathwaydoseswillconsidertheJamesA.Fitzpatrick andNineMilePointUnitIIfacilities aswellasNineMilePointUnitINuclearStation.Inthe'event-thecalculations demonstrate thatthe40CFR190doselimits,asdefinedabove,havebeenexceeded, thenareportshallbepreparedandsubmitted totheCommission within30daysasspecified inSection3.6.15.doftheTechnical Specifications.

~:"'"Section 4.0ofthe'DCMcontainsmoreinformation concerning calculations foranevaluation,of=whether 40CFR190limits.havebeenexceeded.

QtpN@i

3.0 GASEOUSEFFLUENTS

3.lSetpointDeterminations 3.1.1Bas1sStackgasandoffgasmonitorsetpoints willbeestablished suchthattheinstantaneous releaserateofrad1oactive materials ingaseouseffluents doesnotexceedthe10CFR20limitsforannualreleaserate.Thesetpoints willbeactivated iftheinstantaneous doserateatorbeyondthe(land)s1teboundarywouldexceed500mrem/yrtothewholebodyor3000mrem/yrtotheskinfromthecontinuous releaseofradioactive noblegas1nthegaseouseffluent.

Emergency condenser ventmonitorsetpoints willbeestablished suchthatthereleaserateforradioactive materials ingaseouseffluents donotexceedthe10CFR20limitsforannualreleaserateoverthepro)ected longestperiodofrelease.Monitorsetpoints fromcontinuous releasepointsw111bedetermined onceperquarterundernormalreleaseratecond1tions andwillbebasedontheisotopiccomposition oftheactualreleaseinprogress, oranoffgasisotopicdistribution, oramoreconservative defaultcompos1tion specif1ed inthepertinent procedure.

Ifthecalculated "setpoint's

'higherthantheexistingsetpoint, itisnotmandatory thatthesetpointbechanged.Monitorsetpoints foremergency condenser ventmonitorsare'conservatively f1xedat5mr/hrforreasonsdescribed inSections3.1.4and.therefore donotrequire.per1odic recalculations.

Underabnormalsitereleaserateconditions, monitoralarmsetpoints fromcontinuous releasepointswillberecalculated and,ifnecessary, resetatmorefrequentintervals asdeemednecessary byCORMSuperv1sion.

Inpart1cular, contr1butions frombothJAFand'MP-2andtheEmergency Condenser Ventsshallbeassessed.

Dur1ngoutagesanduntilpoweroperation isagainrealized, thelastoperating stackandoffgasmonitoralarmsetpoints shallbeused.

"s~>j 3.1.1(Cont'd)Sincemonitorsrespondtonoblegasesonly,monitoralarmpointsaresettoalarmpriortoexceeding thecorresponding totalbodydoserates.Theskindoseratelimitisnotusedinsetpointcalculations becauseitisneverlimiting.

3.1.2StackMonitorSetpoints Thedetailedmethodsforestablishing setpoints shallbecontained inthestationprocedures.

Thesemethodsshallapplythefollowing "general"criteria:

(1)Rationale forStackmonitorsettingsisbasedonthegeneralequation:

'releaserateactualcorresponding doserate,actualreleaseratemax.allowable corresponding doserate,max.allowable

~E'X/QE(eM)-Mnax500mr/yrwhere:,yCi/secreleasedrateforeachisotope,iX/Qhighestlandsectorsiteboundary(elevated) dispersion parameter (seeTable3-1)Mi3gammaairdosefactorinunitsofmr/yr/yCi/m (SeeTable4-1)(9)instantaneous releaseratelimit.max k+i$Ql<<14 3.1.2(Cont'd)(2)Toensurethat10CFR20andTechnical Specifications doseratelimitsarenotexceeded, thehihialarmsonthestackmonitorsshallbesetlowerthanorequalto(0.9)(Q).Hialarmsmax'hallbesetlowerthanorequalto(0.5)(Q)max(3)Basedontheaboveconservatism, thedose'contribution fromJAFandNMP-2canusuallybeignored.DuringEmergency

'lassifications atJAForNHP-2duetoairborneeffluent, orafteremergency condenser ventreleasesofsignificant proportions, the500mr/yrvaluemaybereducedaccordingly.

(4)ToconvertmonitorgrosscountratestopCi/secreleaserates,thefollowing generalformulasilallbeapplied:(C-B)KQpCi/secreleaseratewhere:CmonitorgrosscountrateincpsorcpmB~-monitorbackground countrateKstackmonitorefficiency factorwithunitsofpCi/sec-cps orpCi/sec-cpm.

(5)MonitorKfactorsshallbedetermined usingthegeneralformula:KsEi(Q)i(C-8)where:individual radionuclide stackeffluentreleaserateasdetermined byisotopicanalysis.

Kfactorsmoreconservative thanthosecalculated bytheabovemethodology maybeassumed.

3.1.2(Cont'd)Alternatively, whenstackreleaseratesarenearthelowerlimitofdetection, thefollowing generalformulamaybeusedtocalculate kf(Yf')~Hdsfwhere:fstackflowincc/secE-effic1ency 1nunitsofcpmcc/pC1orcpscc/pC1Ekcpmcc/bpsorcpscc/gsfromenergycalibration curveproduceddur1ngNBStraceable pr1marygascalibration ortransfersourcecalibration Ykb/d(betas/disintegration) orW/d(gammas/d)

IFiActivityfractionofnuclide1inthem1xturenuclidecounterkdiscreteenergybetaorgammaemitterpernuc11decounters"secondsThismonitorcal1bration methodassumesanoblegas.distribut1on-typicalofarecoilreleasemechan1sm.

To-ensurethatthecalculated efficiency isconservative, betaorgammaemissions whoseenergyisabovetherangeofcalibration ofthedetectorarenotincludedin"*thecalculation.

pl~SI 3.1.3Recombiner Discharge (OffGas)MonitorSetpoints (1)Thehihialarmpointsshallactivatewithrecombiner discharge ratesequaltoorlessthan500,000pCi/sec.ThisalarmpointmaybesetequaltoorlessthanlCi/secforaperiodoftimenottoexceed60daysprovidedtheoffgastreatment systemisinoperation.

(2)Theh1alarmpointsshallact1vatewithrecombiner discharge ratesequaltoorlessthan500,000pCi/sec(3)ToconvertmonitormR/hrreadingstopCi/sec,theformulabelowshallbeapplied:(R)(KR)QRpCi/secrecombiner discharge releaseratewhere:RmR/hrmonitorindicator KRefficiency factorinunitsofpCi/sec/mR/hr determined pr1ortosett1ngmonitoralarmpoints(4)MonitorKRfactorsshallbedetermined usingthegeneral""'formula:

KRwhere:ZQi/R'-individual noblegasradionuclide recombiner

<<;discharge releaserateasdetermined byisotop1canalysisandflowratemon1tor.KRfactorsmoreconservative thanthosecalculated bytheabovemethodology maybeassumed.

Ilf+~~,cg~).gpg~y'g

-.e,+w'~"a~'I 3.1.3(Cont'd)(5)Thesetpoints chosenprovideassurance thatthetotalbodyexposuretoanindividual attheexclusion areaboundarywillnotexceedaverysmallfractionofthelimitsof10CFRPart100intheeventthiseffluentisinadvertently discharged directlytotheenvironment withouttreatment (therebyimplementing therequirements ofGeneralDesignCriteria60and64ofAppendixAto10CFRPart'50).Additionally, thesesetpoints.serve to.limitbuildupoffissionproductactivitywithinthestationsystemswhichwouldresultifhighfuelleakageweretobepermitted overextendedperiods.3.1.4Emergency Condenser VentMonitorSetpointThemonitorsetpointwasestablished bycalculation

("Emergency

,Condenser VentMonitorAlarmSetpoint",

January13,1986,NMPCFileCode816199).Assumingahypothetical casewith(1)reactorwateriodineconcentrations higherthantheTechnical Specification Kimit,(2)reactorwaternoblegasconcentrations higherthanwouldbe'!'~'expected atTechnical Specificationiodine levels,and(3)leakageofreactorsteamintotheemergency condenser shellat300%ofrated6flow(or1.3x10lbs/hr),thecalculation predictsanemergency

.condenser ventmonitorresponseof20mr/hr.Suchareleasewouldresultinlessthan10CFR,20doserate.valuesatthesiteboundary-..-".andbeyondfortypicalemergency condenser cooldownperiods.Sincea20mr/hrmonitorresponsecan,intheory,beachievable onlywhenreactorwateriodinesarehigherthanpermitted byTechnical Specifications, aconservative monitorsetpointof5mr/hrhasbeenadopted.

\lae'1PKg~lqb+~'.~>

~'/iLiatgr,'k\t 3.1.5Discussion 3.1.5.1StackEffluentMonitoring SystemDescription TheNMP-1Stack'Effluent Monitoring Systemconsistsoftwo-subsystems; theRadioactive GaseousEffluentMonitoring System(RAGEHS)andtheoldGeneralElectricStackMonitoring System-(OGESHS).

Duringnormaloperation, theOGESHSshallbeusedtomonitorstationnoblegaseffluents andcollectparticulate andiodinesamplesincompliance withTechnical Specification

,.requirements.

TheRAGEHSisdes1gnedtobepromptlyactivated fromtheMainControlRoomforuseinhighrangemonitoring duringacc1dentsituations incompliance with,NUREG 0737.crtter1a.

Overallsystemschematic fortheOGESHSandRAGEHSareshownonFigureS-9.Asimplified viewofRAGEHSShowingUnit0,1,2,3and4canbefoundonFigureS-8.he'AGEHS canprovidecontinuous accidentmonitor1ng andon-lineisotopicanalysisofNMP-1stackeffluentnoblegasesatLowerLevelsofDetection lessthanTechnical Specificat1on Table4.6.15-2lim1ts..Activities aslowas5X10andash1ghas2-X10pCi/ccfornoblegasesaredetectable bythe'system.

aAgplQ,yrIaviwwpa<~4)~'(~l'f~r~ph~l17/N 3.1.5.2StackSampleFlowPath-RAGEHSTheeffluentsampleisobtainedinsidethestackatelevation 530'singanisokinetic probewithfourorifices.

Thesamplelinethenbendsradiallyoutandbackintothestack;descendsdownthestackandoutofthestackatapproximately elevation 257';runshorizontally (enclosed inheat-tracing) s'ome270'longtheoffgastunnel;andenterstheRAGEHSlocatedontheTurbineBuilding250'Dilution cabinet-Unit0)andOffGasBuilding247'Particulate, Iodine,NobleGasstations-Units1-3).IntheDilutioncabinetoftheRAGEHS,thestackgasmaybedilutedduringaccidentsituations approximately 100-200X(firststage)or10000-40000 X(firstandsecondstage)withgaseousnitrogensupplied-':'romanon-siteliquidnitrogenstoragetank(seeFigure8-9).FromUnit0,'thesamplegasentersUni,t1-3ofRAGEMSandflowsthruin-lineparticulate andiodinecartridges andthenthrueithera6".liter',(low'range) or30cc(highrange)noblegaschamber.ThesamplegasnextflowsbackthruUnit0andtheoffgastunnel;andbackintothestack.

4Oga'%ygNl+y",,>h&g'4 3.1.5.3StackSampleFlowPath-OGESHSTheOGESHSsampleisobtainedfromthesamestacksampleprobeastheRAGEHS.Fromtheexitofthestackatelevation'257',

thesamplelinerunseastapproximately 20'ndthen.vertically approximately 8'otheOGESHSskid.IntheOGESHS,sampleflowsthruaparticulate/iodine cartridge'ousing andfournoblegasscintillation detectors (ie,07and08lowrangebetadetectors and11and12highrangegammadetectors).

FromOGESMS,thestacksampleflowsbackintothestackatapproximately elevation 257'.AllOGESHSdetectoroutputsaremonitored andrecordedremotelyintheHainControlRoom.Alarmingcapabilities areprovidedtoalertOperators ofhighreleaserateconditions priortoexceeding Technical Specification 3.6.15.b(1)adoseratelimits.Stackparticulate andiodines'amplesareretrieved manuallyfromthe.OGESHSandanalyzedinthelaboratory usinggammaspectroscopy at"'"frequencies andLLDs'specified inTable4.6.15-2oftheTechnical Specifications.

p4\/k'(=Np,He'L4s'e>'-6+~v 3.1.5.4,SamplingFrequency/Sample AnalysisRegardless ofwhichstackmonitoring subsystem isutilized, radioactive gaseouswastesshallbesampledandanalyzedinaccordance withthesamplingandanalysisprogramspecified inTechnical Specification Table4.6.15-2.-

Particulate.

samplesare.;,savedandanalyzedforprincipal gammaemitters, grossalpha,Fe-55,Sr-89,Sr.-90atmonthlyintervals minimally.

Thelatterthreeanalysesareperformed off-sitefromacomposite sample.Sample".analysis frequencies are.increased duringelevatedreleaserateconditions, following startup,shutdown,and incon]unction witheach drywellpurge.'-'onsistent withTechnical Specification Table4.6.15-2, stackeffluenttritiumissampledmonthly,duringeachdrywellpurge,andweeklywhenfuelisoffloadeduntilstablereleaseratesaredemonstrated.

Samplesareanalyzedoff-site.

Linelosscorrection factorsareappliedtoallparticulate andiodineresults.Correction factorsof2.0and1.5areusedfordata-obtained fromRAGEHSand.OGESHS respectively.

Thesecorrection factorsarebasedonempirical.

datafrom-sampling conducted, at-NMP-1in1985(memofrom3.BlastaktoRAGEHSFile,1/6/86,"StackSampleRepresentativeness Study:RAGEHSvs.In-StackAuxiliary ProbeSamples").

<<v~ft~t1l~'W~"

3.1.5.5I-133Estimates Monthly,thestackeffluent.shallbesampledforiodinesovera24hourperiodandtheI-135/I-131 andtheI-133/I-131 ratioscalculated.

Theseratiosshallbeusedtocalculate I-133,I-135releaseforlongeracquisition samples-collected duringthemonth.Additionally,-the I-135/I-131 andI-133/I-131 ratiosshouldalsobe5determined afterasignificant changeintheratioissuspected (eg,plantstatuschangesfromprolonged shutdowntopoweroperation orfueldamagehasoccurred).

3.1.5.6GaseousRadwasteTreatment SystemOperation Technical Specification 3.6.16.brequiresthatthegaseousradwastetreatment systemshallbeoperableandshallbeusedtoreduceradioactive materials ingaseouswastepriortotheirdischarge asnecessary tomeettherequirements ofTechnical Specification 3.6.15.b.

ToensureTechnical Specification 3.6.15.blimitsarenotexceeded, andtoconfirmproperradwastetreatment systemoperation as'applicable, cumulative dosecontributions forthecurrentcalendarquarterand'current-calendar."year shallbedetermined monthlyinaccordance withsection3.2ofthismanual.Initialdosecalculations shallincorporate thefollowing assumptions withregardtoreleaseratesofnon-gamma emittingradionuclides subsequently analyzedoff-site:

/t1"~=1B~'IQ 3.1.5.6(Cont'd)a)H-3releaserate)4uCi/secb)Sr-89releaserate)4xCs-137releaseratec)Sr-90releaserate)0.5xCs-137releaserated)Fe-55releaserate)1xCo-60releaserateAssumedreleaseratesrepresent conservative estimates derivedfromanalysisofhistorical datafromeffluentreleasesandprocesswastestreams(SeeNMP34023,C.MaretoJ.Blasiak,April29,1988,"DoseEstimates forBeta-Emitting Isotopes".).

Following receiptofVoff-siteH-3,Sr-89,Sr-90,Fe-55analysisinformation, doseestimates shallberevisedusingactualradionuclide concentrations.

3.2DoseandDoseRateDeterminations Inaccordance withspecifications 4.6.15.b.(2) and4.6.15.b.(3),

doseanddoseratedeterminations willbemademonthlyinordertodetermine:

(1)TotalbodydoseratesandgammaairdosesatthemaximumX/Qlandsector'siteboundaryinterface andbeyond.(2)SkindoseratesandbetaairdosesatthemaximumX/Qlandsectorsiteboundaryinterface andbeyond.(3)ThecriticalorgandoseanddoserateatthemaximumX/Qlandsectorsiteboundaryinterface andatacriticalreceptorlocationbeyondthesiteboundary.~

f',4*4h 3.2(Cont'd)Eitheraveragemeteorological data(ie,maximumfiveyearannualaverageX/QandD/Qvaluesinthecaseofelevatedreleasesor1985annualaverageX/QandD/Qvalues,inthecaseofgroundlevelreleases) orrealtimemeteorological datashallbeutilizedfordoseanddoseratecalculations.

Whereaveragemeteorological dataisassumed,doseanddoseratesduetonoblegasesatlocations beyondthe'iteboundarywillbelowerthanequivalent siteboundarydoseanddoserates.Therefore, undertheseconditions, calculations ofnoblegasdoseanddoseratesbeyondthemaximumX/Qlandsectorsiteboundarylocations canbeneglected-Thefrequency ofdoseratecalculations willbeupgradedwhenelevatedreleaserateconditions specified insubsequent sections3.2.1.1and3.2.1.2arerealized.

Emergency condenser ventreleasecontributions tothemonthlydoseanddoseratedeterminations willbeconsidered onlywhentheemergency condenser returnisolation valveshavebeenopenedforreactorcooldownorifEmergency Condenser tubeleaksdevelopwithorwithoutthesystem'sreturnisolation valveopened.Withouttubeleakageoropeningof,thereturnisolation valves,releasesfromthissystemarenegligible andthecorresponding dosecontributions donothavetobeincluded.

~i'F1(Ik$C>>c!

3.2(Cont'd)'henreleasesfromtheemergency condenser haveoccurred, doseanddo'seratedeterminations shallbeperformed usingmethodology in3.2.1and3.2.2.Furthermore, enviromental samplingmayalsobeinitiated torefineanyactualcontribution todoses.SeeSection3.4.Criticalorgandosesanddoseratesmaybeconservatively calculated byassumingtheexistence ofaso-called "moving"criticalreceptor.

Atthis"moving"criticalreceptorlocation, itisassumedthatall'"*'pa'thways "are.applicable andthehighestX/Qand/orD/QvalueforractualpathwaysasnotedinTable3-1areineffect.Aperson'sdoseatthe"moving"criticalreceptorlocations isequaltothesamedosethatpersonwouldreceiveiftheyweresimultaneously subjected tothehighestpathwaydoseateachcriticalreceptoridentified foreachpathway.Ifdoseordoseratescalculated, usingtheassumptions notedabove,reachTechnical Specification limits,actualpathwayswillbeevaluated, anddose/dose ratesshallbecalculated atseparatecriticalreceptorlocations andcomparedwithapplicable limits.3.2.1DoseRateNotallpathwaysneedbeconsidered indoseanddoseratecalculations ateachcriticalreceptorlocation.

Forexample,when*--"'"calcul'ating landsectorsite.boundarydosesanddoseratesforparticulates, iodinesandtritium,onlythegrounddeposition andinhalation pathwaysapply.

/jism 3.2.1.1NobleGasesIn'accordance withthe-provisions.of 10CFR20thedoseratesfromnoblegasreleasefromthesitetounrestricted areasaretobelimitedto500mrem/yrtotheskin.Doseratecalculation willbeperformed monthly,orwhentheHiHistackmonitoralarmpointisreached,usingthefollowing equations:

Fortotalbodydoserates(inmr/yr):DR+~3.17x10f[Mi(X/Q)Qi/

]Forskindoserates(inmRad/yr):

DR/+a3.17x10~[Ni(X/Q)Qi/sec]

+DR+where:-8Mi,Ni,X/Q,Qi,.3.17x10areasdefinedinsection3.2.2.13.2.1.2Tritium,ZodinesandParticulates (1)Thedoserateinunrestricted areas'rom the'releaseoftritium,iodine-131, iodine-133 andallradionuclides inparticulate formwithhalflivesgreaterthan8daysislimitedto1500mrem/year toanyorgan.

~!',1'I 3.2.1.2(Cont'd)(2)Enordertoensurethat,.the 1500mrem/year doseratelimitisnotexceeded, particulate, iodineandtritiumoffsitedoseratecalculations shallbeperformed monthlyandwheneverparticulate andiodinereleaseratesexceed0.3pCi/secusingtheequationgiveninSection3.2.2.2withQexpressed iniiCi/sec.

Whenthe"releaserateexceeds0.3uCi/sec,thedoserateassessment shallalsoincludeJAFandNMP-2contribution.

(3)Theuseofthe0.3vCi/secreleaseratethreshold toperform""""doseratecalculations is)ustified asfollows:P(a)The1500mrem/yrorgandoseratelimitcorresponds toaminimumreleaseratelimitof0.30nCi/seccalculated usingtheequation:

1500(Q/sec)x(Ri)W))where:1500siteboundarydoseratelimitinmrem/year (Ri)W))"themaximumcurie-to-dose'conversion factorequalto4900mrem-sec/uCi-yr forSr-90,childboneatthe"moving"criticalreceptorlocationbeyondthesiteboundary.

Tp(\pl 3.2.1.2(Cont'd)(b)Theuseof0.3iiCi/secreleaseratethreshold andthe4900mrem-sec/vCi~r curie-torose conversion factorisconservative sincecurie-torose conversion factorsforotherisotopeslikelytobepresentaresignificantly

.lower.Forexample,I-131hasthesecondhighestcurie-to-dose factorequalto465mrem-sec/uCi-yr fortheinfantthyroid.Thiscorresponds toareleaseratelimitofapproximately 3nCi/sec.

3.2.2DoseCalculations willbeperformed monthlyataminimum,todemonstrate thatdosesresulting fromthereleaseofnoblegases,tritium,I-131,I-133andparticulates withhalflivesgreaterthan8daysarewithinthelimitsspecified in10CFR50,AppendixI.Theselimitsare:NobleGasAirDose5mrgamma/calendar quarter10mradbeta/calendar quarter10mrgamma/calendar year'0mradbeta/calendar yearRadioiodines, Tritium&Particulates 7.5mremtoanyorgan/calendar quarter"'15'mrem-to anyorgan/calendar.

year 4NQSiI<<4.4I 3.2.2.1NobleGasAirDose--The-air'doseatthecritical.

receptorduetonoblegasreleasesisdetermined asfollows:Forgammaradfation Dg3.17x107MiX/QForbetaradiation D<~3.17x10E'iX/QQiwhereMairgammadosefactorin(mr/yearperuCi/m)for3i.eachisotopei(Table4-1)3N~airbetadosefactor(mrad/year peruCi/m)foreachisotopei(Table4-1)X/Qtherelativeplumeconcentration (inunitsofsec/m)atthelandsectorsiteboundaryor3beyond.Eitheraveragemeteorological data(Table3-1orAppendixC),orrealtimevaluesmaybeassumed."Elevated" X/Qvaluesareusedforstackreleases; "Ground"X/Qvaluesareusedfor;Emergency Condenser Ventreleases.

Q~thetotalquantityofisotopeireleasedduring.theperiod,(pCi)-83.17x10-~theinverseofthenumberofsecondsinayear.

4V'fe 3.2.2.2Radioiodine, Tritium&Particulates Thedosestoanindividual fromI-131,I-133,tritium,andparticulates withhalflivesgreaterthan8dayswillbecalculated asfollows:-8Dose3.17x10R~EiRi~akW~Qi WhereWJdispersion parameter eitherX/Q(sec/m)orD/Q3(1/m)depending onpathwayandreceptorlocation2assumed.Eitheraveragemeteorological data(Table3-1,orAppendixC)orrealtimevaluesmaybeassumed."Elevated" Wvaluesareusedforstackreleases; "Ground"WvaluesareusedforEmergency Condenser Ventreleases.

thetotalquanityofisotopeireleasedduringtheperiod,(uCi)izaak3':17;x10thedosefactorforeachisotopei,pathwayj,agegroupa,andorgank(Table4-2,through4-20)~theinverseofthenumberofsecondsinayearTheRvaluescontained

.in'Tables,4-2,through 4-20werecalculated usingthemethodology definedinNUREG-0133,and Regulatory Guide1.109,Revision1.

-~4W 3.2.2.3Accumulating DosesDoseswillbecalculated monthly,ataminimum,forgammaairandbetaair,theidentified criticalorgan,andagegroup.Resultswillbesummedforeachcalendarquarterandyear.Ithasbeenhistorically demonstrated thatthecriticalpathwayisusuallythegrass-cow-milk pathwayandthecriticalorganis,the.,,infant',s thyroid.Forthisreason,monthlyinfantthyroiddoseestimates willnormallybemadepriortoreceiptofallanalysisdata(i.e.,strontium andtritium).

Thecriticaldosesarebasedonthe,following pathways:

noblegasplumeairdosegroundplanedose(deposition) inhalation dosecow'smilkdosegoat'smilkdosemeatconsumption dosevegetation (foodcrops)doseThequarterly andannualresultsshallbecomparedtothelimitslistedin'.paragraph 3.2.2.Ifthelimitsareexceeded, specialreports,asrequiredbySection.6.9.3 of-theTechnical Specification, shallbesubmitted.

kl~A~4~gt4p~'J-4Ifi 3.3CriticalReceptors Inaccordance withtheprovisions of10CFR20and10CFR50,AppendixI,thecriticalreceptors havebeenidentified andarecontained inTable3-1..."For...noble gas:doses, one.oftwocriticalreceptorlocations willbeassumed.WhenmaximumfiveyearaverageannualX/Qvaluesareused,thecriticalreceptoristhemaximumX/Qlandsectorsiteboundary1interface.

Whenrealtimemeteorological X/Qvaluesareused,thecriticalreceptormayeitherbethemaximumX/Qlandsectorsiteboundarylocation, orthedownwindlocationofgreatestX/Qresidence (e.g.,1.5mileseast),whichever ishigher.ForI-133,I-131,tritiumandparticulate radionuclides withhalflifegreaterthaneightdays,thecriticalpathwaysaremilk(cowandgoat>,meat,vegetation, inhalation anddirectradiation (groundplane)asaresultofgrounddeposition.

ThecowmilkandgoatmilkpathwaywillbebasedonthegreatestD/Q~...*'ilk,.cow andmilkgoatlocationasdetermined bytechnical specification'.3.6.22.',.The'inhalation

'dosepathway,will.bebased-onthegreatestX/Qresidence asdetermined bytechnical specification 3.6.22sincethislocationwouldhavethegreatestpotential occupancy time.Thegroundplanedosepathwaywillbecalculated asthegreatestD/Qresidence becauseofthegreatestpotential occupancy time.-38" lp4l\Ci$il+i' 3.3(Cont'd)Forthemeatconsumption dosepathway,thecriticalreceptoristhegreatestD/Qmeatanimallocation.

Thislocationhasbeendetermined inconjunction withthelandusecensus(technical specification 3.6.22)andissubjecttochange.Thevegetation (foodcrop)doseisbasedonthegreatest-D/Q gardenlocationfromwhichsamplesare.taken.Thislocationalso.maybemodified:as aresult.of.vegetation samplingsurveys.3.4Refinement ofOffsiteDosesResulting fromEmergency Condenser VentReleasesThedosesresulting fromtheoperation oftheemergency condensers andcalculated inaccordance with3.2.2mayberefinedusingdatafromactualenviromental samples.Grounddeposition sampleswillbeobtainedfromanareaorareasofmaximumprojected deposition.

Theseareasareanticipated tobeat<,<or..near.

thesiteboundaryandnearprojected plumecenterline.

Usingthemethodology foundinRegulatory Guide1.109,thedosewillbecalculated tothemaximumexposedindividual.

Thisdosewillthenbecomparedtothedosecalculated inaccordance with3.2.2.Thecomparison willresult,inanadjustment factoroflessthanor.greaterthanonewhichwillbeusedtoadjust"the'other dosesfromotherpathways.

+jl..LS 3.4(Cont'd)Otherenvironmental samplesmayalsobecollected andtheresultant calculated dosestothemaximumexposedindividual comparedtothedosecalculated per3.2.2.Otherenvironmental samplemediamayincludemilk,vegetation (suchasgardenbroadleaf vegetables),

etc.'"."Theadjustment:factors.

from.these.pathways maybeappliedtothedosescalculated per3;2.2onapathwaybypathwaybasisorseveralpathwayadjustment factorsmaybeaveragedandusedtoadjustcalculated doses.Dosescalculated fromactualenvironmental samplemediawillbebasedonthemethodology presented inRegulatory Guide1.109.Theregulatory guideequations maybeslightlymodifiedtoaccountforshortintervals oftime(lessthanoneyear)ormodifiedforsimplicity purposesbydeletingdecayfactors.Deletionofdecayfactorswouldyieldmoreconservative results.

~~~'a

4.0 40CFR190REQUIREMENTS

The"UraniumFuelCycle"isdefinedin40CFRPart190.02(b)asfollows:-"Uraniumfuelcycle'eans theoperations ofmillingofuraniumore,chemical-conversion ofuranium,isotopic-enrichment ofuranium,fabrication ofuraniumfuel,generation ofelectricity byalight-water-cooled nuclearpowerplantusinguraniumfuel,andreprocessing ofspenturaniumfuel,totheextentthatthesedirectlysupporttheproduction ofelectrical'ower forpublicuseutilizing nuclearenergy,butexcludesminingoperations, operations

.atwastedisposalsites,transportation ofanyradioactive materialinsupport.oftheseoperations, andthereuseofrecovered non-uranium specialrnuclearandby-product materials fromthecycle."Section3.6.15.doftheTechnical Specifications requiresthatwhen~'.thecalculated dosesassociated withtheeffluentreleasesexceedtwicethelimitsofsections3.6.15.a.(2)(b),

3.6.15.b.(2)(b) and3.6.15.b.(3)(b),

thencalculations shallbemadeincluding directradiation contributions fromthereactorunitsand.outside storagetanks(asapplicable)-

todetermine whetherthe40CFR190dose-limitshavebeenexceeded.

~~~"0Eff,ffE'~~IfkEI~'kI'II~PIEQ',WEE,Wt~IFEIFJIfJj4I'00fIJI~~FfFQf 4.0(Cont'd)Ifsuchisthecase,NiagaraMohawkshallsubmitaSpecialReporttotheNRCandlimitsubsequent releasessuchthat.thedosecommitment toarealindividual fromalluraniumfuelcyclesourcesislimitedto<'25mremtothe'total bodyor-anyorgan--(except-the,.thyroid,

'which'islimitedto<..75mrem)overthecalendaryear.Thisreportistodemonstrate thatradiation exposures toallrealindividuals fromalluraniumfuelcyclesources(including allliquidandgaseouseffluentpathwaysanddirectradiation) arelessthanthelimitsin40CFRPart190.Ifreleasesthatresultindosesexceeding the40CFR190limitshaveoccurred, thenavariancefromtheNRCtopermitsuchreleaseswillberequested andifpossible, actionwillbetakentoreducesubsequent releases.

""'"The"reporttotheNRCshallcontain:1)Identification ofalluraniumfuelcyclefacilities or'perations within5milesofthenuclearpowerreactorunitsatthesitethatcontribute to,the-annual doseofthemaximumexposedmemberofthepublic.2)Identification ofthemaximumexposedmemberofthepublicandadetermination ofthetotalannualdosetothispersonfromexistingpathwaysandsourcesofradioactive effluents anddirectradiation.

<<42-J'-~4~>f4p 4.0(Cont'd)Themaximumtotalbodyandorgandosesresulting fromradioactive

-material inliquideffluents fromNineMilePointUnit1will.besummedwiththemaximumdosesresulting fromthereleasesofnoblegases,radioiodines, andparticulates fortheothercalendarquarters~>>~--(as.applicable)...and, from.thecalendar.,quarter in,whichtwicethe..limitwasexceeded.

Thedirectdosecomponents willbedetermined byeithercalculation oractualmeasurement.

Actualmeasurements willutilizeenvironmental TLDdosimetry.

Calculated measurements willutilizeengineering calculations todetermine aprojected directdosecomponent.

Zntheeventcalculations areused,themethodology willbedetailedasrequiredinSection6.9.1.eoftheTechnical Specifications.

ThedosesfromNineMilePointUnit1willbeaddedtothedosestothemaximumexposedindividual thatarecontributed fromotheruraniumfuelcycleoperations within5milesofthesite.Forthepurposeofcalculating doses,'he resultsoftheRadiological Enviromental Monitoring Programmaybeincludedforproviding morerefinedestimates ofdosesto.areal.maximumexposedindividual;..

Estimated doses,ascalculated fromstationeffluents, maybereplacedbydosescalculated fromactualenviromental sampleresults.

~e~~eeee~~~eeeIeeeDEeeeeeeeee Evaluation ofDosesFromLiquidEffluents Fortheevaluation ofdosestorealmembersofthepublicfromliquideffluents, thefishconsumption andshoreline sedimentgrounddosewillbeconsidered.

Sincethedosesfromotheraquaticpathwaysareinsignificant, fi'sh'onsumption'and "shoreline'ediment>>

aretheonly'wopathwaysthatwill-beconsidered.

Thedoseassociated with,fishconsumption maybecalculated usingeffluentdataandRegulatory Guide1.109methodology orbycalculating adosetomanbasedonactualfishsampleanalysisdata.Thedoseassociated withshoreline sedimentisbasedontheassumption thattheshoreline wouldbeutilizedasarecreational area.ThisdosemaybederivedfromliquideffluentdataandRegulatory Guide1.109methodology orfromactualshoreline sedimentsampleanalysisdata.Equations usedtoevaluatedosesfromactualfishandshoreline sedimentsamplesarebasedonRegulatory Guide1.109methodology.

.Because.

ofthesamplemediumtypeandthehalf-lives oftheradionuclides historically

observed, thedecaycorrected portionsoftheequations aredeleted.Thisdoesnotreducetheconservatism ofthecalculated dosesbutincreases thesimplicity fromanevaluation pointofview.Thedosefromfishsamplemediaiscalculated as:(1)Rwb~Fi[Cifxux1000xDiwbxf]Where:~Thetotaldosetothewholebodyofanadultinmremperyear.

A<<+t%eA (Cont'd)Cif~Theconcentration ofradionuclide iinfishsamplesinpCi/gram.

~Theconsumption rateoffishforanadult(21kgperyear).1000~Gramsperkilogram'Diwb~Thedosefactorforradionuclide::i forthewholebodyofanadult(R.G.1.109,TableE-11).~Thefractional portionoftheyearoverwhichthedoseisapplicable.

(2)RlWhere:~~i[Cifxyx1000xDilx~Thetotaldosetotheliverofanadult(maximumexposedorgan)inmremperyear.Cif=Theconcentration ofradionuclide iinfishsamplesinpCi/gram.

~Theconsumption rateoffishforanadult(21kgperyear).1000~GramsperkilogramDil~Thedosefactorforradionuclide ifortheliverofanadult(R.G.1.109,TableE-ll)~Thefractional portionoftheyearoverwhichthedoseisapplicable.

Thedosefromshoreline sedimentsamplemediaiscalculated as:Where:-E[Ci,xllx-40,000x0.3xDiwbxf]and~g[Cisxyx40,000x0.3xDiskxf]~Thetotaldosetothewholebodyofateenageroradult(maximumexposedagegroup),inmremperyear.Rsk~Thetotaldosetotheskinofateenageroradult(maximumexposedagegroup)inmremperyear.Cis~The-concentration ofradionuclide iinshoreline sedimentinpci/gram.

4"0AgR)i"I (Cont'd)~Theusagefactor.Thisisassumedas67hoursperyearbyateenageroradult.I40,000~Theproductoftheassumeddensityofshoreline sediment(40kilogrampersquaremetertoadepthof2.5cm)timesthenumberofgramsperkilogram.

0.3~Theshorewidthfactorforalake,Diwb=The'dosefactorfor'radionuclide iforthetotal,body(R.G.1.109,TableE-6)Disk~Thedosefactorforradionuclide ifortheskin(R.G.1.109,TableE-6)~Thefractional portionoftheyearoverwhichthedoseisapplicable.

NOTE:"'ecauseofthenatureofthereceptorlocationandtheextensive fishingactivityinthearea,thecriticalindividual-may beateenageroranadult.

Qb.~iiIh'4*~~~'ial4lhkgtlXfCkingil0~iii\f1E1'h'4gt0tl~iit4 4.2Evaluation ofDosesFromGaseousEffluents Fortheevaluation ofdosestorealmembersofthepublicfromgaseouseffluents, thepathwayscontained insection3.2.2.3oftheODCMwillbeconsidered.

Theseincludetheingestion, inhalation and'deposition pathways'.

However,anyupdatedfield:data may.beutilizedthatconcernslocations ofrealindividuals, realtimemeteorological data,locationofcriticalreceptors, etc.Datafromthemostrecentcensusandsamplelocationsurveysshouldbeutilized.

Dosesmayalsobecalculated fromactualenviromental samplemedia,asavailable.

Enviromental samplemediadatasuchasTID,airsample,milksampleandvegetable (foodcrop)sampledatamaybeutilizedinlieuofeffluentcalculational data.Dosestomemberofthepublicfromthepathwasycontained inODCMsection3.2.2.3asaresultofgaseouseffluents willbecalculated usingthedosefactorsofRegulatory Guide1.109orthemethodology

"."oftheODCM,asapplicalble.

Dosescalculated fromenvironmental samplemediawillutilizethemethodologies foundinRegulatory Guide1.109.4.3Evaluation ofDosesFromDirectRadiation Section3.6.15.doftheTechnical Specifications requiresthatthedosecontribution asaresultofdirectradiation beconsidered whenevaluating whetherthedoselimitations of40CFR190havebeenexceeded.

1,*i"Prf+'<w+X g'~Itplyg Directradiation dosesasaresultofthereactor,turbineandradwastebuildings andoutsideradioactive storagetanks(asapplicable) maybeevaluated byengineering calculations orbyevaluating enviromental TLDresultsatcriticalreceptorlocations, siteboundaryorotherspecialinterestlocations.

Forthe"evaluation ofdirectradiation-doses-utilizing environmental'-TLDs,

-':the'ritical receptorinquestion, suchasthecriticalresidence, etc.,willbecomparedtothecontrollocations.

Thecomparison involvesthedifference inenvironmental TLDresultsbetweenthereceptorlocationandtheaveragecontrollocationresult.4~4DosestoMembersofthePublicMithintheSiteBoundary.

Section6.9.l.eoftheNineMilePointUnit1Technical Specifications requiresthattheSemiannual Radioactive EffluentReleaseReport~include anassessment oftheradiation dosesfromradioactive liquidandgaseouseffluents tomembersofthepublicdue.to.their=,activities insidethesiteboundaryasdefinedbyFigure5.1-1ofthespecifications.

Amemberofthepublic,asdefinedbytheTechnical Specifications, wouldberepresented byanindividual whovisits"thesites'nergy Information Centerfor.thepurposeofobserving theeducational displaysorforpicnicing

.andassociated

...activities.

>>r<<III~>>rn<<>>y>>f04~>>4s0V~<<.g<<g*WWy--,'>>>>>><<

I~>><<,S>><<S'4P~"gag,>>

4~4(Cont'd)Fishingisamajorrecreational activityintheareaandontheSiteasaresultofthesalmonidandtroutpopulations inLakeOntario.Fishermen havebeenobservedfishingattheshoreline neartheEnergyInformation CenterfromAprilthrough"December inallweather'onditions."

'Thus,"fishingis-the'ajor activityperformed bymembersofthepublicwithinthesiteboundary.

Basedonthenatureofthefishermen andundocumented observations, itisconservatively assumed'hatthemaximumexposedindividual spendsanaverageof8hoursperweekfishingfromtheshoreline atalocationbetweentheEnergyInformation CenterandtheUnitlfacility.

Thisestimateisconsidered conservative butnotnecessarily excessive andaccountsforoccasions whereindividuals mayfishmoreonweekendsoronafewdaysinMarchoftheyear.Thepathwaysconsidered fortheevaluation includetheinhalation

""-pathway withtheresultantlung dose,thegrounddosepathwaywiththeresultant wholebodyandskindoseandthedirectradiation dosepathwaywiththeassociated totalbodydose.Thedirectradiation dosepathway,in.actuality, includesseveralpathways.

Theseinclude:thedirectradiation gammadosetoanindividual fromanoverheadplume,agammasubmersion plumedose,possibledirectradiation dosefromthefacilityandagroundplanedose(deposition).

Becausethelocationisincloseproximity tothesite,anybetaplumesubmersion doseisfelttobeinsignificant.

'iAW'II~4I'I~.(-I.lI"~p~II++II.>>l~Ili~gWyrIN'i~"Iwl~fI 4~4(Cont'd)Otherpathways, suchastheingestion pathway,arenotapplicable.

Inaddition, pathwaysassociated withwaterrelatedrecreational activities, otherthanfishing,arenotapplicable here.Theseincludeswimming,'oating andwadingwhichareprohibited atthe~facility.

Theinhalation pathwayisevaluated byidentifying theapplicable radionuclides (radioiodine, tritiumandparticulates) intheeffluentfortheappropriate timeperiod.,Theradionuclide concentrations arethenmultiplied bytheappropriate X/Qvalue,inhalation dosefactor,airintakerate,andthefractional portionoftheyearinquestion.

Thus,theinhalation pathwayisevaluated usingthefollowing equationadaptedfromRegulatory Guide1.109.NOTE:Thefollowing equationisadaptedfromequations C-3andC-4ofRegulatory Guide1.109.SincemanyofthefactorsareinunitsofpCi/m,,m/sec.,etc.,andsincethe33Fradionuclide decayexpressions havebeendeletedbecauseoftheshortdistancetothereceptorlocation, theequation...presented here,is.,not.identical

.totheRegulatory Guideequations.

R~y.i[CFX/QDFA.Rt]ii]aawhere:Rthemaximumdosefortheperiodinquestiontothelung(j)forallradionuclides

<i)fortheadultagegroup<a)inmrempertimeperiod.

4~fPIIIk~s,A 4'(Cont'd)The'average concentration inthestackreleaseofradionuclide iinpCi/mfortheperiodinquestion.

3F~Unit1averagestackflowrateinm/sec.3'X/Q.The:plume dispersion"parameter foralocationapproximately 0.50mileswestofNMP-1(Theplumedispersion parameter is8.9E-06andwasobtainedfromtheC.T.MainfiveyearaverageannualX/Qtables.AX/Qvaluebasedonrealtimemeteorology mayalsobeutilizedfortheperiodinquestion, ifdesired.Thestack(elevator)

X/Qisconservative whenbasedon0.50milesbecauseofthecloseJproximity ofthestackandthereceptorlocation).

DFAi)theinhalation dosefactorforradionuclide i,thelungj,andadultagegroupainmremperpCifoundonTableE-7ofRegulatory Guide1.109.Raannualairintakeforindividuals inagegroupainMperyear(thisvalueis8,000mperyearand33wasobtained.fromTableE-5ofRegulatory Guide1.109).fractional portionoftheyearforwhichradionuclide-iwasdetectedandforwhichadoseistobecalculated (inyears).

I$tVhH,~t'rP4)+'%Su' Thegrounddosepathway(deposition) willbeevaluated byobtaining atleastonesoilorshoreline sedimentsampleintheareawherefishingoccurs.Thedosewillthenbecalculated usingthesampleresults,thetimeperiodinquestion, andthemethodology basedonRegulatory Guide1.109aspresented inSection4.1.Theresultant dosemaybeadjustedforabackground-dose bysubtracting the""-applicable

-off-si'te controlsoilor=shoreline sedimentsampleradionuclide activities.

Intheeventitisnotedthatfishingisnotperformed fromtheshoreline, butisinsteadperformed inthewater(i.e.,theuseofwaders),thenthegrounddosepathway(deposition) willnotbeevaluated.

Thedirectradiation gammadosepathwayincludesanygammadosesfromanoverheadplume,submersion intheplume,possibleradiation fromthefacilityandgroundplanedose(deposition).

Thisgeneralpathwaywillbeevaluated byaverageenvironmental TI,Dreadings.

Atleasttwoenvironmental TIDswillbeutilizedatonelocationinthe'approximate areawherefishingoccurs.TheTIDswillbeplacedinthefieldonapproximately thebeginning ofeachcalendarquarterandremovedonapproximately theendofeachcalendarquarter(quarter2,3,and4),.TheaverageTLDreadingswillbeadjustedbytheaveragecontrolTLDreadings.

Thisisaccomplished bysubtracting theaveragequarterly; controlTI.DvaluefromtheaveragefishinglocationTLDvalue.Theapplicable quarterly controlTLDvalueswillbeutilizedafteradjusting fortheappropriate timeperiod(asapplicable).

ZntheeventoflossortheftoftheTLDs,resultsfromaTLDorTLDsintheareamaybeutilized.

l,RIk-)Lj'bgrjf

5.0 ENVIRONMENTAL

MONITORING PROGRAM5'SamplingStationsThecurrentsamplinglocations arespecified inTable5-1andFiguresS.l-l,5.1-2.Themeterological towerisshowninFigure5.1-1.The.locationisshownas"TLD'ocation 17.TheRadiological Environmental Monitoring ProgramisajointeffortbetweentheNiagaraMohawkPowerCorporation andtheNewYorkPowerAuthority, theownersand,operators oftheNineMilePointUnit1andtheJamesA.FitzPatrick NuclearPowerPlant,respectively.

Samplinglocations arechosenonthebasisofhistorical averagedispersion ordeposition parameters frombothunits.Theenvironmental samplinglocationcoordinates shownonTable5-1arebasedontheNMP-2reactorcenterline.

Theaveragedispersion anddeposition parameters havebeencalculated fora5yearperiod,1978through1982.Thesedispersion

'"""-'calculations areattachedasAppendixC.Thecalculated dispersion ordeposition parameters willbecomparedtotheresultsoftheannuallandusecensus.Ifitisdetermined thatamilksamplinglocationexistsatalocationthatyieldsasignificantly higher(e.g.50%)calculated D/Qrate,thenewmilksamplinglocationwillbeaddedtothemonitoring programwithin30days~Ifanewlocationisadded,theoldlocationthatyieldsthelowestcalculated D/QmaybedroppedfromtheprogramafterOctober31ofthatyear.

~Ef 5.2Interlaboratory Comparison ProgramAnalysesshallbeperformed onsamplescontaining knownquantities ofradioactive materials thataresuppliedaspartofaCommission approvedorsponsored Interlaboratory Comparison Program,such,asthe"EPACrosscheck'Program."-Participation shallbeonly'orthosemedia,e.g.,air,milk,water,etc.,-thatareincludedintheNineMilePointEnvironmental Monitoring Programandforwhichcrosscheck samplesareavailable.

AnattemptwillbemadetoobtainaQCsampletoprogramsampleratioof5%orbetter.Thesiteidentification symbolortheactualQualityControlsampleresultsshallbereportedintheAnnualRadiological Environmental Operating ReportsothattheCommission staffmayevaluatetheresults.SpecificsamplemediaforwhichEPACrossCheckProgramsamplesareavailable includethefollowing:

~grossbetainairparticulate filters-~'ammaemittersinairparticulate filtersI-131inmilkgammaemittersinmilk-gammaemittersinfoodproductgammaemittersinwatertritiuminwaterI-131inwater v'$g$A)Ifan%f'~1 5.3Capabilities forThermoluninescent Dosimeters UsedforEnvironmental Measurements Requireddetection capabilities forthermoluminescent dosimeters usedforenvironmental measurements requiredbyTable4.6.20-1, footnoteb'*'-.oftheTechnical Specifications-,iare..based.;,on.

ANSIStandard.N545,';~..-.>

'",section4;3."-'"TLDsare'efined asphosphors packagedforFielduse.>,'nregardtothedetection capabilities forthermoluminescent dosimeters, onlyonedetermination isrequiredtoevaluatetheabove.~capabilities pertypeofTLD.Furthermore, theabovecapabilities maybedetermined bythevendorwhosuppliestheTLDs.Requireddetection capabilities areasfollows:5.3.1Uniformity shallbedetermined bygivingTLDsfromthesamebatchanexposureequaltothatresulting fromanexposurerateof10uR/hrduringthefieldcycle.Theresponses obtainedshallhavearelativestandarddeviation oflessthan7.5%.Atotalofatleast5TLDs4i,'~"shallbe.evaluated.

5.3.2Reproducibility shallbedetermined bygivingTLDsrepeatedexposures

'"equalto,thatresulting fromanexposurerateof10uR/hrduringthe'ieldcycle.The..average, oftherelative'standard" deviations of,theresponses shallbelessthan3.0%.htotalofatleast4TLDsshall,beevaluated.

f}IIIl4e 5.3.3Dependence ofexposureinterpretation onthelengthofafieldcycleshallbeexaminedbyplacingTLDsforaperiodequaltoatleastafieldcycleandaperiodequaltohalfthesamefieldcycleinanareawheretheexposurerateisknowntobeconstant.

Thistestshallbeconducted underapproximate averagewintertemperatures, and,:approximate average..summertemperatures.

Forthesetests,.theratio'oftheresponse"-obtained inthefieldcycletotwicethatobtainedforhalfthefieldcycleshallnotbelessthan0.85.Atleast6TLDsshallbeevaluated 5.3.4'nergydependence shallbeevaluated bytheresponse.ofTLDstophotonsforseveralenergiesbetweenapproximately 30keVand3MeV.Theresponseshallnotdifferfromthatobtainedwiththecalibration

'sourcebymorethan25%forphotonswithenergiesgreaterthan80keVandshallnotbeenhancedbymorethanafactoroftwoforphotonswithenergieslessthan80keV.Atotalofatleast8TLDsshallbeevaluated.

5.3.5Thedirectional dependence oftheTLDresponseshallbedetermined bycomparing theresponseoftheTLDexposedintheroutineorientation

'*'"withrespecttothecalibration sourcewiththeresponseobtainedfor"'di'fferent

-orientations;

  • To"accomplish this,-the, TLD-shall.be.,rotated throughatleasttwoperpendicular planes.'heresponseaveraged-overalldirections shallnotdifferfromtheresponseobtainedinthestandardcalibration positionbymorethan1(C.Atotalofatleast4TLDsshallbeevaluated.

~<4~g.'t 5.3.6Lightdependence shallbedetermined byplacingTLDsinthefieldforaperiodequaltothefieldcycleunderthefourconditions foundinANSIN545,section4.3.6.Theresultsobtainedfortheunwrapped TLDsshallnotdifferfromthoseobtainedfortheTLDswrappedinaluminumfoilbymorethan10K.Atotalofatleast4TLDsshallbeevaluated foreachofthefourconditions.

5.3;7'Moisture'dependence'shall"be-determined"by-placing=TLDs.(that is,the.phosphors~packaged "forfielduse)foraperiodequaltothefield,...-

cycleinanareawheretheexposurerateisknowntobeconstant.

TheTLDsshallbeexposedundertwoconditions:

(1)packagedinathin,sealedplasticbag,and(2)packagedinathin,sealedplasticbagwithsufficient watertoyieldobservable'oisture throughout the.fieldcycle.TheTLDorphosphor, asappropriate, shallbedriedbeforereadout.TheresponseoftheTLDexposedintheplasticbagcontaining watershallnotdifferfromthatexposedintheregularplasticbagbymorethan10X.Atotalofatleast4TLDsshallbeevaluated foreachcondition.

'."5;3".8.-

"a'Self.irradiation shallbedetermined byplacingTLDsforaperiodequaltothefieldcycleinanareawheretheexposurerateislessthan10uR/hrandtheexposureduringthefieldcycleisknown.Ifnecessary,.corrections shallbeappliedforthedependence of'exposureinterpretation on*thelengthofthefieldcycle(ANSIN545,.section4.3.3).The'average exposureinferredfromtheresponses of-theTLDsshallnotdifferfromtheknownexposurebymorethananexposureequaltothatresulting fromanexposurerateof10uR/hrduringthefieldcycle.Atotalofatleast3TLDsshallbeevaluated.

IfI<<gr TABLEl-lRVALUESFORTHENINEMILEPOINTUNIT1FACILITYapjiNUCLIDE89Sr90Sr134Cs137Cs58Co60Co54HCr-51Fe-59Zn-65Zr-95I-131I-133Cs-136Ba-140Ce-141'e-55Ni-63ADULT-TOTALBODYR~i{MREM/YR-Cx 2.05E-34.37E-11.89E+01.12E+06.47E-41.85E-32.72E-37.40E-74.05E-63.01E-31.09E-l1.69E-73'4E-43.53E-52'3E-13..92E-55.49E-93.47E-43.41E-3TEEN-LIVER-,I-"N/AN/A2.35E+01.78E+02.87E-48.38E-41.40E-25.69E-7N/A8.03E-32.37E-12.53E-76.65E-41.22E-43.80E-17.81'-75.17E-8.1.60E-37.46E-3<<58-

,1tl4f(

TABLE1-2PARAMETERS FORTHELIQUIDEFFLUENTPATHWAYPARAMETER UapMpBipDaipiVALUEAdult~21.0Kg/yrTeen16.0Kg/yr0.2590,ft./second.EachElementEachradionuclide REFERENCE (REG.GUIDE1.109)TableE-5SiteSpecificSiteSpecificTableA-1TablesE-lltoE-14Tp26.9hoursSiteSpecific II',leAcP~Ak.

TABLE2-1AverageEnergyPerDisintegration ISOTOPEAr-41Kr-83mKr-85Kr-85mKr-87Emev/dis1.2940.002480.00220.1590.793~Ref(3)EBmev/dis(4 0.4640.03710.2500.2531.325Ref)(3)Kr-881.950.377Kr-89Kr-90Xe-131MXe-133Xe-133mXe-135Xe-135m2.22'2.100.02010.04540.0420.2470.432(2)(2)1.371.010.1430.1350.3.90.3170.095(2)(2)Xe-137Xe-1380.194l.18'.640.611(1)ORNL-4923, Radioactive Atoms-SulementI,M.S.Martin,November1973.(2)NEDO-12037, "SummaryofGammaandBetaEmittersandIntensity Data";M.E.""',".Meek,R.S.'Gilbert, January1970.(The.averageenergy..was computedfrom-'themaximumenergyusing.theICRPIIequation,.

notthe.1/3value..assumption usedinthisreference).

(3)NCRPReportNo.58,"AHandbookofRadioactivity Measurements Procedures";

1978(4)Theaverageenergyincludesconversion electrons.

fII"lQaI4"4~~~

LOCATIONResidences DairyCowsMilkGoatsMeatAnimalsGardensSiteBoundaryDIRE(98O)SE(1300)E(88')ESE(115)E(97m)ENE(67)MILES1.42.67.91.81.80.41.8E-07b2.2E-08c1.3E-08c5.1E-08c1.0E-07c2.4E-06bDdD~/m-25.2E-09b7.0E-10c1.6E-10c17E09c3.5E-09c4.4E-08cDdTABLE3-1CriticalReceptorDispersion Parsmetersa ForGroundLevelandElevatedReleasesELEVATEDELEVATEDGROUNDe'4.02E-076.00E-082.57E-081.16E-072.53E-076.63E-06GROUNDeD/I/Dm~8.58E-091.64E-096.10K-103.54E-095.55E-096.35E-08a.Thesevalueswillbeusedindosecalculations beginning inApril1986butmayberevisedperiodically toaccountforchangesinlocations offarms,gardensorcriticalresidences.

b.Valuesbasedon5yearannualmeteorological data(C.T.Main,Rev.2)c.Valuesbasedon5yearaveragegrazingseasonmeteorological data(C.T.MainRev.2)d.Valuearebasedonmostrestrictive X/Qland-based sector(ENE).(C.T.Main,Rev.2)e.Valuesarebasedonaverageannualmeteorological datafortheyear1985.

~"q TABLE4-1DOSEFACTORSPORNOBLEGASESRadionuclides Kr-83mKr-85mKr-85Kr-87Kr-88Kr-89Kr-90Xe-131mXe-133mXe-133Xe-135mXe-135Xe-137Xe-138Xe-139Ar-41GammaAirDoseFactorMiBIZdpCi-yr1.93E+011.23E+031.72E+016.17E+031.52E+041.73E+041.63E+041.56E+023.27E+02353E+023.36E+031.92E+031.51E+039.21E+035.28E+039.30E+03BetaAirDoseFactorNimradmpCi-yr2.88E+021.97E+031.95E+031.03E+042.93E+031.06E+047.83E+031.11E+031.48E+031.05E+037.39E+022.46E+031.27E+044.75K+036.52E+043.28E+03*Regulatory Guide1:109,"'Calculation ofAnnualDosestoManFromRoutine.-.ReleasesofReactorEffluents forthePurposeofEvaluating Compliance with10CPRPart50,Appends.x I,"datedOctober1977,page1.109-21.

4p$ell~"Ib$IIh eTABLE4-2RVALUES-COW'SMILK-INFANT2md~rem/ruCi-secNUCLIDEH3"Cr51Mn54Fe55Fe59Co58Co60Zn65Sr80Sr90Zr95I131I133CH134Cs136Cs137Ba140Ce141em~rem/ruCi/mT.BODY2.40803GI-TRACT2.40E031.458077.218072.888071.11E085.268091.708081.798105.588026.928087.918063.598091.038092.378095.948061.448036.918068.748072.888071.128089.638091.22808Se758083.92E055.628074.578069'5E074.19E071.048082.838076.30E067.468042.178064.548067.36806BONE8.438071.05E083.32E095.948097.018103.238031.348091.85E071.908109.37E082.858101.158082.00804LIVER2.408032.008075.448071..158074.71E071.148107.878021.57E092.708073.558102.768093.348101.158051.22804KIDNEY2.40E031.068044.44E065.53E09Be48E021.848093'78079.14E091.10E098.968092.74E043.76E03THYROID2.408034.878045.178ll4.91809LUNG2.408034.478042.66807)5.418073.758092.258.083.638097.03804

~SX44IJ~~gtp ThBLE4-3RVhLUES-COM'SMILK-CHILD2m~~remjrQCi-secNUCLIDEH3>Cr51Mn54Pe55Pe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136CQ137Ba140Ce141~m~remlruCi/m3T.BODY1.58E034.71B042.87E061.15E074.52E071.77E076.81S074.10E098.93E071.63B103.56B023.66E084.11S064.09E098.53E082.52B093.27E067.47B02CI-TRhCT1.58E032.50S069.04E066.85E069.45B073.37E071.28E081.16S091.21S088.68E084.17E055.73E074.38E061.05B084.63E071.07B082.84B076.28E06BONE6.97E075.61E072.47E093.13E096.44$101.82S036.40E088.78E061.18E104.80S081.79E105.60E071.01E04LIVER1.58E031.08B073.07E079.08E075.77S062.31E076.59E094.00E026.44E081.09E071.94E101.32E091.71E104.91E045.03E03KIDNEY1.58E037.14E033.02S064.15E095.72E021.06E091.81E076.01E097.07S085.57B091.60E042.21E03THYROID1.58E032.61E042.13Ell2.02E09LUHC1.58S03)<4.77E042.09E072.63E072.16E091.05E082.00S092.93E04 Ir,"8)\~ff4/!,gtp4 TABLE4-4RVALUES-COW'SMILK-TEEN2m~~rcimleuCi-secNUCLIDE83>Cc'1Mn54Fe55Pe59Co5&Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136Cs137Ba140Ce141*miamiuCi/m3T.BODY1.00E2.31E0304&.10E3.35E2.04E3.62E9.42E06070907091.70E021.98E1.87E5.60E5.62B3.44E1.5&E0806090809063.14E021.43B064.59E062.1&E07GI-TRACT1.00E033.88E061.4&E078.52B061.34E085.21E071.94E081.85E091.50E081.07E095.70E057.31E074.64B061.50E086.73E071.40E083.5&E077.83E06BONE,1.5&E032.7&E072.42E071.26E091.26E093.81E107.83E022.64B083.61E065.12E092.13E087.42E092.32E074.10E03LIVER1.00E031.20E061.97E075.65E073.78E061.49E074.3&E092.47E023.69B086.13E061.21E108.37E089.87E092.84E042.74E03KIDNEY1.00E035.06E032.15E062.&OE093.63E026.36E081~0&E073.83E094.55E083.36E099.65E031.29E03THYROID1.00E031.2&E041.0&Ell8.56E08LUNG1.00E033.30E041.25E071.7&E071.46E097.1&E071.30B091.91E04 llIplxg5.iJ TABLE4-5RVALUES-COM'SMILK-ADULT2md~rem/uci-secNUCLIDEH3~Cr51Mn54Pe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134CQ136Cs137Ba140Ce141>m~rsmlruci/mT.BODY7.69E021.32E048.25E052.52E061.25E075.03B061.93E071.18S091.97B076.62E099.72E011.19E081.05E065.74E093.55E083.65E098.43E051.71E02GI-TRACT"7.69S023.32E061.32E076.21E061.09B084.56B071.65B081.65E091.10E087.80S084.55E055.49E073.09E061.23E085.60E071.08E082.65E075.78E06SONS1.57E071.39E078.21E086.85E082.70E104.48E021.45E081.98E062.95E091.25E084.09E091.29E072.24E03LIVER7.69E024.32E061.08E073.26E072.24E068.77E072.81E091.44B022.08E083.44E067.02E094.93E085.59E091.62E041.51E03KIDNEY7.69E022.91S031.29E061.75E092.25E023.57E086.01E062.27E092.74E081.90E095.49E037.02E02THYROID7.69E027.90E036.82E105.06B08LUNG7.69E021.75E046.04E069.10B067.54E083.76E076.31E089.25S03

~el'V~,J/

TABLE4-6RVALUES-GOAT'SHILK-INFANT2mm~eemleuCi-secNUCLIDSH3~Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136CQ137Ba140Ce141em~eemleuCi/m3T.BODY4.90E038.95B035.45E051.89S059.37E053.45B061.34E07&.31S083.58E083.57E106.70E018.31E089.49E061.08E103.09E097.10S09e7.13E051.72E02GI-TRACT4.90B032.61E058.83E058.98E041.14B063.45E061.35E071.16E092.57E081.84E094.70E046.74E075.48E062.89E081.26E083.13E083.40E067.57E05BONE1.10E061.36E063.99E081.25E101.47E113.88E.021.60E092.23E075.71E102.81E098.55E101.38E072.40E03LIVER4.90S032.40E067.08E052.38E061.38E065.65S061.37E099.45EOl1.89E093.24E071.07E118.27E091.00E111.38E041.46E03KIDNEY4.90E031.28E035.33S056.63E081.02E022.21E093.81E072.74E103.30B092.69E103.29S034.52E02THYROID4.90E035.84B036.21Ell5.89S09LUNG4.90E031.14E043.46B057.03B051.12E106.74E081.09E108.50E03 qlI04i$:~I'<~rLOFTlg1I~N"'+i'51 TABLE4-7RVALUES-GOAT'SMILK-CHILD2m~~ramlruCi-secNUCLIDEH3"Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136Cs137Ba140Ce141*m~rrmjruCi/mT.BODY3.23E035.65E033.44E051.49E055.88B052.12E068.17E064.92S081.87B083.43E104.27E014.39E084.93E061.23E102.56S097.57E093.92E058.97E01GI-TRACT3.23E033.00B051.08E068.91E041.23E064.04E061.53E071.39E082.54B081.82E095.01S046.88E075.25B063.14E081.39E083.21B083.41E06:7.54E05BONE9.06E057.29E052.97B086.56S091.35Ell2.18S027.68E081.05E073.55E101.44E095.36E106.72E061.21E03LIVER3.23E03i1.29E064.81E051.18E066.92E052.77E067.91E084.80E017.72E081.30E075.82E103.96E095.13E105.89E036.04E02KIDNEY3.23E~038.57E023.62E054.98E086.87E011.27S092.17E071.80E102.11E091.67E101.92E032.65E02THYROID3.23E033.14E032.55Ell2.42E09LUNG3.23E035.73E032.72E053.42E056.47E093.14E086.01E093.51S03 V&IkP*1yEr1)~g ThBLE4-8RVhLUES-GOhT'SMILK-TEEN2m~~rmm/uCi-seeNUCLIDBH3"Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134CH136Cs137BR140Ce141*m~ram/uCi/m3T.BODY2.04E032.77S031.71E055.97B042.83E051.04B064.02E062.45E087.59S071.98B102.04E012.38B082.24S061.68E101.69S091.03E101.80E053.77EOlGI-TRhCT2.04E034.66B051.77E061.11E051.74B066.25E062.32E072.22S083.16E082.25E096.84E048.77E075.57E064.50E082.02E084.21E084.30E069.39E05BONE3.61E053.14E051.51E082.65E098.81B109.40EOl3.17B084.34B061.54E106.38E082.22E102.97E064.92E02LIVER2.04E038.64E052.56E05KIDNEY2.04E036.07E022.58E052.97E014.43E087.36E063.62E102.51B092.96E103.41E033.28E024.36EOl7.63E081.29E071.15E101.37E091.01E101.16E031.55E027.34E054.63E051.78E065.25E083.36E08THYROID2.04E031.54E031.29Ell1.03E09LUNG2.04E033.95E031.62E05I42.31E054.39E092.15E083.91E092.30E03 II(1JhJ0 TABLE4-9RVALUES-GOAT'SMILK-ADULT2mm~eemluci-secNUCLIDEH3"Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136Cs137Ba140Ce141em~rem/uCi/mT.BODY1.57E031.59E039.89E043.28E041.62E056.03E052.32E061.42E084.13E071.39E101.17EOl1.43E081.26B061.72E101.06E091.10E101.01E052.06E01GI-TRACT1.57E033.99E051.59E068.07E04'1.41E065.46E061.98B071.97E082.31E081.64E095.46E046.59E073.71B063.69E081.68E083.25E083.18E066.94B05BONEe2.04E051.80E059.85B071.44E095.67E105.37E.Ol1.74E082.37E068.85E093.75E081.25E101.54E062.68E02LIVER1.57E03e5.19E051.41E054.23E052.69E051.05E063.14E081.72E012.50E084.13E062.11E101.48E091.68E101.94E031.81E02KIDNEY1.57E033.49E021.54E052.10E082.70EOl4.28E087.21E066.82E098.23E085.70E096.59E028.43EOlTHYROID1.57E039.48E028.18E106.07E08LUNG1.57E032.11E037.85E04I1.18E052.26E091.13E081.89E091.11E03 Ptr1Ci TABLB4-10RVALUES-MEAT-CHILD2m~~remlruCi-secNUCLIDEH3<Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136Cs137Ba140Ce141em~rem/ruCi/m3T.BODY2.36B024.07E031.09E064.74B071.42E082.39B071.09E083.72B08.6.55E061.52E092.48E054.64E061.55B-011.67E081.35B071.04B081.22B067.57E02GI-TRACT2.36B022.16E053.45B062.84B072.97B084.56E072.05E081.05E088.87E068.08B072.91E087.29E051.66E-Ol4.26E067.34B054.43B061.06B076.36B06BONE2.89B081.76B082.25E082.29$086.00E091.27B068.14B063.32B-014.81B087.60E067.39B08gelOE071.02B04LIVER2.36E024.11E061.53E082.85E087.82E063.70E075.99E082.79E058.19E064.11B-017.90B082.09E077.07B081.84E045.10E03KIDNEY2.36E026.17E021.15E063.77E083.99E051.34B076.85B-012.45E081.11E072.30E085'8E032.24E03THYROID2.36B022.26E032.71B097.63E-01LUNG2.36E024.12B038.66B07)'.26E078.78B071.66E068.29E071.10E04 J'WPwp,tg.yl'Ip4 TABLE4-11RVALUES-MBAT-TEEN2m~~remlruCi-secNUCLIDECr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136CB137Ba140Ce141em~rem/ruCi/m3T.BODY1.95E022.61E037.12E052.49E078.95E071.54E077.03E072.43B083.47E061.15E091.55E053.30E069.25E-022.98E081.16B071.86B087.33E054.14E02GI-TRACT1.95E024.39E057.37E064.62E075.48B089.22E074.06E082.20E081.44E071.30E085.20E081.22E062.30E-017.99E061.40E067.59E061.75E071.04E07BONE1.50E089.93E071.50E081.21E084.64E097.15E054.39E061.79E-012.73E084.41E064.01E081.14E075.43E03LIVER1.95E023.59E061.07E082.32E086.69E063.12E075.20E082.25E056.14B063.03E-016.42E081.73E075.34B081.39E043.63E03KIDNEY1.95E025.72E021.07E063.33E083.31E051.06E075.32E-012.04E089.44E061.82E084.72E031.71E03THYROID1.95E021.45E031.79E094.23E01LUNG1.95E023.73E036.77E0747.31E077.78E071.49E067.06E079'7E03 tCAr4r TABLE4-12RVALUES-MEAT-ADULT2md~rem/ruCi-secNUCLIDEH3~Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133CH134Cs136Cs137Ba140Ce141*m~remlruCi/mT.BODY3.27E023.26B038.98E052.98E071.12E081.95E078.87B073.06E084.12E061.76E091.94E054.33E061.13E-Ol6.68E081.61E074.33E089.01B054.96E02GI-TRACT3.27B028.21E051.44E077.34B079.73B081.76E087.56E084.27B082.30E072.07B089.07E081.99E063.34E-011.43E072.53E061.28B072.83E071.67B07BONE1.85E081.24E082.13E081.43E087.17E09'.92E055.28E062.14E-013.43E085.65E064.83E081.38K076.47E03LIVER3.27E024.71E061.28E082.92E088.68E064.02E6.78E07082.86E057.55E063.72E-018.15K082.23E076.61E081.73E044.38E03KIDNEY3.27B027.19E021.40E064.53E084.49E051.29E076.49B-012.64E081.24E072.24E085.87E032.03E03THYROID3.27E021.95K032.48E095.46E01LUNG3.27E024.33$037.14B07].8.16E078.78E071.70E067.46E079.89E03 AT ThBLE4-13RVhLUES-VSGSThTION

-CHILD2md~rem/ruCi-secNUCLIDEH3*Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Se90Zr95I131I133Cs134Cs136Cs137Ba140Ce141em~rem/ruCi/m3T.BODY4.048031.168051.73E081.258083.17E081.928081.118091.70S091.03E093.498ll7.448058.168071.678065.408091.438083.528091.618074.75E04GI-TRhCT4.048036.15E065.44E087.50E076.628083.668082.088094.818081.408091.868108.718081.288071.788061.388087.77E061.50E081.408083.99808BONE7.638083.938081.03E093.62810'.388123.808061.438083.578061.568108.048072.488102.768086.42E05LIVER4.048036.498084.05E086.36E086.278063.768082.748098.358051.44E084'28062.568102.218082.398102.428053.20E05KIDNEY4.048031.768041.82E081.738091.208062.368087.368067.93E091.18E087.78E097.878041.40E05THYROID4.048036.448044.758108.21808LUNG4.048031.188052.29808141.848082.848091.768072.808091.44805 F4-0c4~'r.elf/~'~

eThBLE4-14RVhLUES-VEGEThTION

-TBEN2.m~~eemleuci-secNUCLIDEH3>Cr51Hn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134CQ136Cs137Ba140Ce141*deem/euCi/m3T.BODY2.61E036.11E048.79E075.13E071.60E089.79E075.57E088.68B084.36E082.05Ell3.68E055.77E071.01E067.54E091.13E084.90B098.88E062.12E04GI-TRhCT2.61E031.03E079.89E089.53B079.78E085.85E083.22E097.88E081.81E092.33E101.23E092.13B072.51E062.02E081.35B072.00B082.12E085.29E08HONE3.10E081.77E085.36E081.52E108.32Ell1.69E.067.68E071.96E066.96E094.28E071.06E101.38E082.77E05LIVER2.61E034.43E082.20E084.14E084.25E072.47E081.86E095.35B051.07E083.32E061.62E101.68E081.41E101.69E051.85E05KIDNEY2.61E031.34E041.32E081.19E097.86E061.85E085.83E065.16E099.16E074.78E095.72E048.70E04THYROID2.61E033.39E043.14E104.64E08LUNG2.61E038.72E041.40B08IE1.30E081.97E091.44E071.86E091.14E05 S>>I'rIrVt"iP1tS"4ktAaJ+lyt0 eTABLE4-15RVALUES-VEGETATION

-ADULT2m~~remlruCi-secNUCLIDEN3<Cr51Mn54Fe55Pe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134CB136Cs137Ba140Ce141em~rem/uCi/m3T.BODY2.28E03GI-TRACT2.28S033.22S071.12E086.71E073.67E085.77S082.87E081.64Ell2.51S056.61E071.12S068.83E091.19E085.94E098.40E061.48E047.91E079.75S086.07E083.12$098.04E081.60E091.93S101.17E093.04E073.30E061.89E081.88E071.76E082.64E084.99E084.60E041.16E075.83E079.36E08BONE2.00E081.24E084.01E081.08E106.70Ell1.16E068.07E072.11E064.54E094.19E076.63E091..28E081.93E05LIVER2.28E033.05S081.38S082.93E082.99E071.66E081.28E093.71E051.15E083.67E061.08S101.66E089.07E091.61E051.$1E05KIDNEY2.28E031.01E049.09E078.54E085.82E051.98E086.40E063.49E099.21E073.08E095.47E046.07E04THYROID2.288032.75E043.78E105.39E08LUNG2.28E036.10E047.69E07<8.17E071.16E091.26E071.02E099.22E04

~Otktl4!a TABLE.4-16RVALUES-INHALATION

-INFANTI~ram/ruCi/m3NUCLIDEH3Cr51Mn54Pe55Fe59CoSsCo60Zn65Sr89Sr90Zr95I131I133CQ134Cs136Cs137Ba140Ce141T.BODY6.468028.938014.988033.338039.468031.82E031.188043.108041.148042.598062.03804I1.968045.598037.448045.288044.548042.898031.99803GI-TRACT6.468023.568027.058031.098032.478041.118043.188045.138046.398041.318052.178041.068032.158031.338031.438031.338033.83E042.15804BONE1.978041.358041.938043.978054.OSSO71.158053.798041.328043.968054.828045.4SSOS5.59E042.77804LIVER6.468022.538041.178042.368041.228038.018036.258042.788044.438041.92E047.02E051.348056.118055.598011.66804KIDNEY6.46E021.328014.98E033.248043.10E045.178042.248041.908055.638041.728051.348Ol5.24803THYROID6.468025.758011.488073.55806LUNG6.468021.288049.98E058.698041.018067.768054.508066.468052.038061.128071.758067.958041.178047.128041.59806P5.16805

%W\4"pCC>4r ThBLB.4-17RVhLUES-INHhLhTION

-CHILDmasm/ruCi/m3NUCLIDBH3Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133CQ134CQ136CQ137Ba140Ce141T.BODY1.128031.548029.508037.778031.678043.168032.268047.028041.728046.438063.698042.728047.688032.248051.168051.288054.328032.89803CI-TRhCT1.128031.088032.298042.878037.068043.438049.618041.638041.678053.438056.108042.848035.478033.848034.178033.618031.028055.65804BONE4.748042.078044.258045.998051.018081.908054.808041.668046.50E056.508049.058057.398043.92E04LIVER1.128034.298042.528043.348041.778031.318041.138054.178044.808042.038041.01S061.718058.248056.478Ol1.95804KIDNEY1.128032.43E011.008047.138045.958047.878043.378043.308059.538042.828052.118Ol8.53803THYROID1.128038.538011.628073.84806LUNG1.128031.708041.57S061.118051.278061.10E067.068069.948052.158061.478072.238061.218051.458041.048051748061*5.43805 V4'>>I~<<kA~I<<ff,*Ifl>>'>>-<<ArI<<4>>,~'>>>>N>>I7g>>

TABLE4-18RVALUES-INHALATION

-TEENm~mamimuCi/m3NUCLIDEH3Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133CH134Cs136Cs137Ba140Ce141T.BODY1.27E031.358028.398035.548031.438042.778031.98E046.238041.25E046.678063.158042.648046.218035.488051.378053.118053.518032.16803GI-TRACT1.278033.008036.678046.398031.788059.518042.598054.668043.718057.648051.498056.488031.038049.758031.098048.478032.288051.26805BONE3.348041.598043.858044.348051.08E081.458053.548041.218045.028055.148046.698055.468042.84804LIVER1.27E035.108042.388043.698042.078031.518041.338054.588044.908042.05E041.138061.938058.478056.698011.89804KIOMEY1.278033.078Ol1.278048.63E046.738048.39E043.59E043.75E051.108053.048052.248Ol8.87803THYROID1.278037.498011.468072.92806LUNG1.27E032.098041.988061.24805'.538061.348068.718061.248062.41E061.65E07=-2.688061.468051.778041.218052.038066.13E05 k~I+vs.f1 TABLE4-19RVALUES-INHALATION

-ADULTm~rem/ruC1/m,3eNUCLIDEH3Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95I131I133Cs134Cs136Cs137Ba140Ce141T.BODY1.268039.998Ol6.29E033.948031.058042.078031.488044.658048.718036.09E062.328042.058044.518037.278051.10804GI-TRACT1.268033.32E037.72E046.038031.888051.068052.848055.348043.498057.218051.508056.278038.878031.048041.17E042.568031.53E032.188051.20E054.27E058.39803BONE2.468041.17804.3.248043.048059.91E071.078052.528048.638033.728053.908044.788053.908041.99804LIVER1.268033.958041.708042.778041.588031.158041.03E053.44E043.578041.488048.478051.468056.208054.908Ol1.35804KIDNEY1.268032.288019e838036e898045.418046.12E042.588042e878058.558042.22E051.678Ol6.25E03THYROID1.26E035.948Ol1.198072.15806LUNG1.268031.448041.4087.2181.01806pgc069.758041.208047.518041.278063.618059.278055.968068.638051.408069.59E061.77806 lpga TABLE4-20RVALUES-GROUND-ALLAGEGROUPS2M~modem/e>>Ci/secNUCLIDE1.BODYCr51Mn54Fe55Fe59Co58Co60Zn65Sr89Zr95I.131I133~.Cs134Cs136Cs137"Ba140'Ce141,I135Ba/La140Nb95Sb1254.66E061.34E092.75E083.79E082.15E107.49E082.23E042.49E081.72E072.47E066.82E091.49E081.03E102.05E071.36E07LaterLaterLaterLater PYf4401etr"'g'i,~

NineMilePointNuclearStationRadiological Environmental Monitoring ProgramSamplingLocations Table5.1TypeofSample*MapLocation(Env.Collection SiteProamNo.)LocationRadioiodine andPaxticulates (air)NineMilePointRoadNorth(R-1)1.8mi888'Radioiodine andParticulates (aix')Co.Rt.29&LakeRoad(R-2)1.1mi8104'SERadioiodine andParticulates (air)Co.Rt.29(R-3)1.5mi8132'ERadioiodine andParticulates (air)VillageofLycoming, NY(R-4)1.8mi8143'E"Radioiodine andParticulates (air)5.MontarioPointRoad(R-5)16.4mi842'EDirectRadiation (TLD)6DirectRadiation (TLD)7DirectRadiation (TLD)8DirectRadiation (TLD)9DirectDirectRadiation (TLD)10Radiation (TLD)llDirectDirectRadiation (TLD)15Radiation (TLD)16DirectRadiation (TLD)12.DirectRadiation (TLD)13.DirectRadiation (TLD)14NorthShoreline Area(75)NorthShoreline Area(76)NoxthShoreline Area(77)NorthShoreline Area(23)JAPEastBoundary(78)Rt.29(79)Rt.29(80)MinerRoad(81)MinerRoad(82)LakeviewRoad(83)LakeviewRoad(84)0.1mi85'0.1mi825'NE0.2mi845'E0.8mi870'NE1.0mi890'1.1mi8115'SE1.4mi8133'E1.6mi8159'SE1.6mi8181'1.2mi8200'SW1.1mi8225'WDirectRadiation (TLD)17DirectRadiation (TLD)18~p-SeeFigures5.1-1and5.1-2SiteMeteorological Tower(7)0.7mi8250'SWEnergyInformation Center(18)0.4mi8265' I"IllI'i~IrFJgAQt+!8W+'

NineMilePointNuclearStationRadiological Environmental Monitoring ProgramSamplingLocations Table5.1(Continued)

TypeofSample*MapLocation(Env.Collection SiteProgramNo.)LocationSurfaceWater39DirectRadiation (TLD)19'DirectRadiation (TLD)20DirectRadiation (TLD)21DirectRadiation (TLD)22DirectRadiation (TLD)23DirectRadiation (TLD)24Direct'adiat'ion"(TLD) 25DirectRadiation (TLD)26DirectRadiation (TLD)27DirectRadiation (TLD)28DirectRadiation (TLD)29DirectRadiation (TLD)30DirectRadiation (TLD)31DirectRadiation (TLD)32DirectRadiation (TLD)33DirectRadiation (TLD)34DirectRadiation (TLD)35DirectRadiation (TLD)36'irectRadiation (TLD)37SurfaceWater38NorthShoreline (85),NorthShoreline (86)NorthShoreline (87)HickoryGrove(88)LeavittRoad(89)Rt.104(90)Rt.51A(91)MaidenLaneRoad(92)Co.Rt.53(93)Co.Rt.1(94)LakeShoreline (95)Phoenix,NYControl(49)S.W.Oswego,Control(14)Scribe,NY(96)AlcanAluminum, Rt.1A(58)Lycoming, NY(97)NewHaven,NY(56)W.Boundary, BibleCamp(15)LakeRoad(98)OSSInletCanal(NA)JAFNPPInletCanal(NA)0.2mi8294'NW0.1mi8315'W0.1mi8.341'NW4.5mi897'4.1mi8ill'SE4.2mi8135'E4-8mi8156'SE44mi8183'64.4mi8205'SW4.7mi8223'W4.1mi8237'SW19.8mi8170'12.6mi8226'W3.6mi8199'SW3.1mi8220'W1.8mi8143'E5.3mi8123'SE0.9mi8237'SW12mi8101'7.6mi8235'W05mi870'NE(NA)~notapplicable

  • Map~See'igures 5.1-1and5.1-2 Jgv*l11I"~IISI NineMilePointNuclearStationRadiological Environmental Monitoring ProgramSamplingLocations Table5.1'Continued)

TypeofSample*Map(Env.LocationCollection SiteProramNo.)LocationShoreline SedimentFishFishFishMilkMilkMilkFoodProductFoodProductFoodProductFoodProductFoodProductFoodProductFoodProduct(CR)404142:43,44454647484950515254SunsetBayShoreline (NA)NMPSiteDischarge Area(NA)NMPSiteDischarge Area(NA)OswegoHarborArea(NA)MilkLocation850MilkLocation87MilkLocation816MilkLocation865ProduceLocation86**(Bergenstock)

(NA)ProduceLocation81**(J.Parkhurst)

(NA)ProduceLocation82<+(Vitullo)

(NA)ProduceLocation85*"(C.S.Parkhurst)

(NA)ProduceLocationIII3**(C.Narewski)

.Produce'Location 84**(S.Morris)(NA)ProduceLocation87*"(McMillen)(NA)1.5mi880E0.3mi8315'Wand/or0.6mi855'E6.2mi8235'W9.3mi893'5.5mi8107'SE5.9mi8190'17.0mi8220'W1.9mi8141'E1.8mi896'1.9mi8101'1.5mi8114'SE1.6mi884'2.0mi8-110'SE15.0mi8223'W 1dw,lVCI'E4J'Fc>lI NineMilePointNuclearStationRadiological Environmental Monitoring ProgramSamplingLocations Table5.1(Continued)

TypeofSample*Map(Env.Location"Collection Site"'-"ProamNo.)-.LocationFoodProduct'(CR)55:.Produce.Location/$8"*(Denman)(NA)12.6mi8225'WFoodProduct'oodProductFoodProductFoodProduct56575859ProduceLocation/P9"*(O'onnor)

(NA)..ProduceLocation810**(C.L~on)(NA)ProduceLocation811**(C.R.Parkhurst)

(NA)ProduceLocation812*"(Johnson)

(NA)1.6mi6171'2.2mi8123'SE2.0mi8112'SE1.9mi8103ESE6CI*Map-SeeFigures5.1-1and5.1-2**FoodProductSamplesneednotnecessarily becol1ected fromalllistedlocations.

Collected sampleswillbeofthehighestcalculated siteaverageD/Q.(N/A)~notapplicable CR~ControlResult(location)

  • =y"QPr.lY<g~lk 141$I4<o~Ap(IIFIGURE5.(-IHinoMllePointOn.SiteMepgfIOweaewolSWlych'4WJshI>caS%SW~I~NO%/ii111$1$141$I015'I t,"p*,"<~.(4,'e'Et*'>.~<(+tV'II1rlWt"qg'h~q~h*f

~t(ltIti~.llillNt I~~tpl0O0CQPl'llEPlOPl

.r4.JA$tt,sAW+t,O~"C'1+Il APPENDlX-ADOSEPARAMETERS FORlODlNE131AND'l33gPARilCULATESANDTBlTl0liras-88-'-

tt4,HAh0+49&TIiAw.jL<rW$sa'~'s't~TI4IWl44,1;)hes&2-"ii~r~w"y~~~"y4'~M~'I~vI'Q DOSEPAiUMETERS FORIODINE-131AND-L33iPARTICULATES ANDTRITIUMThisappendixcontainsthemethodology whichwasusedtocalculate thedoseparameters forI-L31,I-L33,particulates, andtritium..The doseparameter, Ri,was-calculated usingthemethodology outlinedinNUREG&L33 and'Regulatory "GuideL.L09,.Revision'L.-.

The-radioiodine andparticulate Technical

.-.;.Specification (Section3.6.15)isapplicable tothelocationintheunrestricted areawherethecombination ofexistingpathwaysandreceptorage~i..groupsindicates, themaximumpotential exposureoccurs,i.e.,thecriticalreceptor.

Theinhs1ation andgroundplaneexposurepathwaysareconsidered toexistatalllocations butthecriticallocationwillbeusedfordosepurposes.

Thegrass-goat-misc, thegrass-cow mQ3c,grass-caveat, andvegetation pathwaysareconsidered toexistatspecificlocations.

Rivalueshavebeencalculated fortheadult,teen,childandinfantagegroupsforallpathways.

Themethodology usedtocalculate thesevaluesfoLlows:i,,:.',.,,'i,,A.L,Inhalation PathwaR.~K(BR)(DFA)where~+~dosefactorforeachidentified radionuclide ioftheorganofinterest(units-~mrem/hrperyCi/m);K'BR)(DFA),,'a'constant ofunitconversion:

-10pCi/qCi;6~Breathing rateofthereceptorofagegroupa,(unitsM/yr);3organinhalation'dose.factor forradionuclide iforthereceptorofagegroupa,(units~mrem/pCi).

89-mr~~tW:L~e4q1t+,iA

~;Thebreathing rates(BR)forthevariousagegroups,asgiveninTableaE-5ofRegulatory Guide1.109Revision1,aretabulated below.AeGrou(a)BreathinRate(m~/yr)InfantChildTeen-Adult1rr00370080008000lnhalatron dosefactors(DFA.)forthevariousagegroupsaregiveninia"TablesE-7throughE-10ofRegulatory Guide1.109Revision1.A.2GroundPlanePathwaI(R=K'K"(SF)DFGiXIt(Im)where:GRidosefactorforthegroundplanepathwayforeachIdentified radionuclide ifOrtheorganofinterest(units=mrem/yrperuCI/secperm)K'.a-constant ofunitconversion:

10pCI/uCi;6K"=aconstantofunitconversion;8760hr/year; g4Il.l0 theradiological decayconstantforradionuclide i,(units=sec)t=theexposurettme,sec;484.73x10sec(ISyears);DFC.,=thegroundplanedoseconversion factorforradionuclide i;(units=mrem/hrperpCi/m~)e'F=theshielding factor(dlmensionless);

IAshielding factorof0.7isdiscussed inTableE-15ofRegulatory Cuide1.109Revision1.Atabulation ofDFGivaluesispresented inTableE-6ofRegulatory Guide1.109Revisionl.A.3Grass-Cow orCoat-Milk Pathwa-AltfRi-K'QFUF(DFL)eYI+B.(1-e.(I-ff)~ps,tr(tm'YEi+Bi(lmth)ewhere:MRl=dosefactorforthecowmilkorgoatmilkpathway,foreach""'"'identified radionuctide

fortheorganofinterest, (unitsmrem/yrperuCi/secperm)..

0l5~"~4~-I~e'ue't@IE K'aconstantofunitconversion:

10pCi/uCi6.QF=Thecow'sorgoat'sfeedconsumption rate,(units=Kg/day-wet weight)Uhereceptor's milkconsumption rate'or-age groupa,(units=liters/yr);

Ytheagricultural product<vity byunitareaofpasturefeedgrass,(units=kg/m~,);.YItheagricultural productivity byunitareaofstoredfeed,(units=kg/m~);thestableelementtransfercoefficients, (units=pCi/liter perpCi/day);

r=fractionofdeposited activityretainedoncow'sfeedgrass:(DFL)=theorganingestion dosefactorforradlonuclide iforthereceptorinagegroupa,(units=mrem/pCi);

'heradiological decay-constant for.radionuclide-

-i,(units=sec);thedecayconstantforremovalofactivityonleafandplant.surfacesbyweathering

~75.73-x10sec.,(corresponding toa10day.half-life);,

.

~rtl~qna tfthetransport timefromfeedtocoworgoattomilk,toreceptor, (units=sec);th=thetransport timefromharvest,tocoworgoat,toconsumption, (units=sec);tb=periodoftimethatsoilisexposed.to gaseouseffluents, (units=sec);8.concentration factorforuptakeofradionuclide ifromthesoilbytheediblepartsofcrops,(units=pCi/Kg(wetweight)perpCi/Kg(drysoil);P=effective surfacedensityforsoil,(units=Kg(drysoil)/m~);

f=fractionoftheyearthatthecoworgoatisonpasture*;

f="fractionofthecowfeedthatispasturegrasswhilethecowisonpasture;t=periodofpasturegrassandcropexposureduringthegrowingseason,(units"-sec);<<Milkcattleandgoatsareconsidered tobefedfromtwopotential sources,pasturegrassandstoredfeeds.Following thedevelopment inRegulatory Cuide1;109Revision1,thevalueoffwasconsidered unityinlieuofs,p'site-specifi

.information.

Thevalueoffwas.0.667.basedupon,an8-monthgrazingperiod.TableA-1containstheappropriate valuesandtheirsourceinRegulatory Cuide1.109Revision1.Theconcentration of>>tritiuminmilkisbasedontheairborneconcentration ratherthanthedeposition.

Therefore, theRiisbasedonX/Q:R=KsKts'FQU(DFL)075(05/H)

'l4Awvvml'lsk%k

}cher.e:MRTdosefactorforthecoworgoatmilkpathwayfortritiumfortheorganofinterest, (units=mrem/yrperuCi/m');K'"=aconstantofunitconversion; l0~gm/kg;H=absolutehumidityoftheatmosphere, (units"-gm/m~);0.75=thefractionoftotalfeedthatiswater;0-5=theratioofthespecificactivityofthefeedgrasswatertotheatmospheric water.,.OCOthervaluesaregivenabove.AvalueofHof8grams/meter3, wasusedinlieuofsite-specific information.

A.OCrass-Cow-Meat Pathwa-XitfRiK'~Fap"YXEi+B.(1m(l-ff)r(lmetb+8(leiv)KithesEiR~=ldosefactorforthemeatingestion pathwayforradlonuclide ifor.-anyorgan:ofinterest, (units."-

mrem/yrperuCi/secperm):-2.F<=thestableelementtransfercoefficients, (units=days/Kg):

=S>>I\11lf,~4l~g)AVIPAIIQf4tg}eV~~@Ok>t apthereceptor's meatconsumption rateforagegroupa.(units=kg/year;t=thetransport timefromslaughter toconsumption, (units=,sec);the,transport time-.from.,harvest..

to,animal"consumpt>on.

-(units=sec):t=periodofpasturegrassandcropexposureduringthegrowingseason,(units=sec)""'"'"All'other"<terms-remain'the.same asdefinedforthemilkpathway.TableA-2containsthevalueswhichwereusedincalculating R..iTheconcentration oftritiuminmeatisbasedonairborneconcentration ratherthandeposition.

Therefore, theRiisbasedonX/Q.RT=K'K"'FfQU(DFLi)(0.75(0.5/H)

Jwhere:dosefactorforthemeatingestion pathwayfortritiumforanyorganofinterest.

(units=mrem/yrperuCl/m~).,.Alltermsaredefinedabove.A.SVetationPathwaTheintegrated concentration invegetation consumedbymanfollowstheexpression developed for.milk.Manisconsidered toconsumetwotypesofvegetation (freshandstored)thatdifferonlyinthetimeperiodbetweenharvestandconsumption, therefore:

(Ifih.%'4gAle4.

R.,"-K'(DFL)XitLUfeaLtlm+YIElPX1-X.tbwhere:S'ithUafgetr(l-e)YAhi-AtB(leib),R,=dosefactor.forvegetable pathwayforradionucllde ifortheorganofinterest, (units=mrem/yrperuCi/secperm);K'aconstantofunitconversion; l0pCi/uCi:6LUa=theconsumption rateoffreshleafyvegetation bytherecepCorinagegroupa,(units=kg/yr);fL=thefractionoftheannualintakeoffreshleafyvegetation grownlocally;fgthefractionoftheannualintakeofstoredvegetation grownlocally~..tL...=.,Che.,average

.timebetween,harvest--ofleafyvegetation anditsconsumption,.

(units=sec);theaveragetimebetweenharvestofstoredvegetation anditsconsumption, (units=sec);Y-thevegetation areadensity,(units=kg/m~);t=periodofleafyvegetable exposureduringgrowingseason(units=sec);

~7I Allotherfactorsaredefinedabove.TableA-3presentstheappropriate parameter valuesandtheirsourceinRegulatory Guide1.109Revision1.Inlieuofsite-specific data,valuesforfL.and;fof,1.0'nd'.76,'respectively, wereusedinthecalculation.

ThesevalueswereobtainedfromTableE-15ofRegulatory Guide1.109Revision1.Theconcentration oftritiuminvegetation isbasedontheairborneconcentration ratherthanthedeposition.

Therefore, theR.isbased'onI.X/Q:R=K'K"TUf+UfaLag(DFL)0.75(0.5/H) where:VRTdosefactorforthevegetable pathwayfortritiumforanyorganofinterest, (units=mrem/yrperuCI/m~).Atlothertermsaredefinedinpreceeding sections.

JlR~~i'o4~1Ik4[5I TABLEA-1Parameters forCowandGoatMilkPathwaysParameter QF(kg/day)Y(kg/m~)tf(seconds)

Value50(cow)6(goat)0.71.73x10(2days)1.0(radioiodines) 0.2(particulates)

  • Reference (R.,Guide1.109Rev.1)TableE-3TableE-3TableE-15TableE-15TableE-15TableE-15(DFL)(mrem/pCi)

F(pCl/dayperpCi/liter) t(seconds)

Y(kg/m~)Y(kg/m~)t(seconds).

U"(liters/yr) t(seconds)

Eachradionuclide Eachstableelement0.73x10(15yr)2.00.77.78x10(90days)330infant330child000teen310adult2.59x106(pasture) 65.'18x10(storedfeed)TablesE-11toE-14TableE-1(cow)TableE-2(goat)TableE-15TableE-15TableE-15TableE-15Table'-5TableE-5TableE-5TableE-5TableE-15Bl(pCl/Kg (wetweight)Each-stableelementperpCi/Kg(drysoil))TableE-IP(Kgdrysoil/m~)200TableE-15 IIg+~a~A'.4it@'PCPV TABLEA-2aParameters fortheMeat.PathwayParameter Ff(pCi/KgperpCi/day)U(Kg/yr)apValue',1.0(radioiodines) 0.2(particulates)

Eachstableelement0infant01child.65teen110adultReference (R.Cuide1.109Rev.1)TableE-15TableE-15TableE-1TableE-5TableE-5TableE-5TableE-5,a(DFL)(mrem/pCi)

Y(kg/m~)Y(kg/mi)tb(seconds) t(seconds)

.t(seconds) t.-(seconds) 1QF(kg/day)B.,(pCi/Kg(wetweightperpCi/Kg(drysoil))P(Kg(dry=soil)/m~)

Eachradionuclide 0.72.01.737.782.595.1850x10x10x10x1066x10(15yr)(20days)(90days)(pasture)

(storedfeed)200EachstableelementTablesE-11toE-14TableE-15TableE-'lSTableE-15TableE-15TableE-15TableE-15TableE-3TableE-1TableE-15-99-I 4)e"'C/'i TABLEA-3Parameters fortheVegetable PathwayParameter r'(dimensionless)

(DFL)(mrem/Ci)

U(kg/yr)-infant-child*-teen-adultU(kg/yr)-infantS~-child-teen-adultt<.(seconds) t(seconds)

Y(kg/m~)t(seconds)

'"t"'(seconds)

~P(Kg(drysoil)/m~)81~(pCl/Kg(wetweight)perpCi/kg(drysoll))Value1.0(radioiodines) 0.2(particulates)

Eachradionuclide 026A%2640520630'208.6x10(1day)5.18x10(60days).2.05.18x10(60days).."Oe73x10.(15yr)82aoEachstableelementReference (R.Guide1.109Rev.1)TableE-1TableE-1TablesE-11toE-10TableE-5TableE-5TableE-5TableE-5TableE-5TableE-5TableE-5TableE-5TableE-15TableE-15TableE-15TableE-15TableE-15TableE-15TableE-1;.-.100-IV~"PEP4pih APPENKNX-B";-'NGRAMSOPLNUlDANDGASEOUSRNDNASTETREATMENT SYSTEMS.10.1 PO'I4~rtdpeP4ygCg~,<cyq0+>~>aI+'gifyl\'I(c,4%

0-CVtaslsIC~4aaph¹Ss¹IOK(t¹hllsllt

~lit,t¹¹,IID<<penis~elIIIIIOIOILIKt0cene¹~sweep4(40~IKwnOatahspic~twin~IW'CCKIKKICLKLC~KKIKKsnle~Ia~IP(ItteOPItt~ISlKLIllaeIC~I~I0I~Itt~~I~~IVKOKOsn~0PplplwG.IwsTRuwEwt AwOEoulpwfwT svvBOLss.((SII(KVI~~ISallIlPl~II~~~I~III~I~!~~s11~~~a(~spt~a(4la~II~I~C(f1ssVa'VIIIa9.OLVA(VtStat(1IL-vol-4(0'K4(saasaae4>>s0(sli~IKPQI'POCP~PK¹atKIVCII'I1stKtl'0SnsPKSILIIY~¹1easSOIWIP(tl(Kstas0L¹(4(etCKI+>140(PeOseSPVCIIS~IIC/vs~t",¹nIL'saKIO(pa~rata140thtt01LStle~Catha(0SVIale~isa'4Iln~I¹I~4'er\LPPI¹sIIsICO¹(IIDIPtlllC044allt¹IIO0~C¹faCPal(IlesQb)4aleII~IVa(p¹4+paaoavKsa~aa'D4(4thOC~t'IK>ip<xoovspn~its(~LO4Pa'p0Xnas(DIDPItsl~LoIp'ctpsKLxoaxLclwpPNIYHQ}tggQ.~AV

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NOTESTOFIGUREB1(a)NHP1Stack(heightis350')(b)NMP2Stack(heightis430')(c)JAFNPPStack(heightis385')(d)NMPlRadioactive LiquidDischarge (LakeOntario,bottom)(e)NHP2Radioactive LiquidDischarge (LakeOntario,bottom)(f)JAFNPPRadioactive LiquidDischarge (LakeOntario,bottom)(g)SiteBoundary~(h)LakeOntarioShoreline (i)Meteorological Tower(j)TrainingCenter(k)EnergyInformation CenterAdditional Information:

-NMP2ReactorBuildingVentislocated187feetabovegroundlevel-.JAFNPPReactorandTurbineBuildingVentsarelocated173feetabovegroundlevel-JAFNPPRadwasteBuildingVentis112feetabovegroundlevel-TheEnergyInformation Centerandadjoining picnicareaareUNRESTRICTED

.'-4.AREAS"within;,the, SITE~BOUNDARY.

thatareaccessible toHEHBERSOFTHEPUBLIC-LakeRoad,aprivateroad,isanUNRESTRICTED AREAwithintheSITEBOUNDARYaccessible toMEMBERSOFTHEPUBLIC5-6 I~II)>>$I'~llh'.AP>>h)">>"

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APPENDlX.-C DfSPERStONCALCULATION TABt.ES @~i'O'I~klfgjfg'Ilp'JLfgel4iIC TABLEC-1D/qTABLE(ANHVALMETEOROLOGICAL DATA)NNPUNIT+ISIACKCORREC'IKD FOROPENTERRAINRECIRCULATION tooeeryoooooottooo ~toRELATIVEDKPDSTjlDHPERUNlTDIRECTIDHFRONSITE.So.I.oo1.50e.oo.8>1.040E-0$ 3.2608-09 I.RC<E-I9 6.78)E-IO SSl)1.806E-OB'3.78TE-09 I.<CRE-O'9 T.STIE-IO SD7.14IE-09R.4038-099.852E-I~5.413K-IILJSD2.169K-09V.C32E"II3.843K-III.835E-II,wR.<56E-09 8.59)flo3.CSIE-IO R.OBSE-IO DND5.076E-09 1.74<E-09 7.<3bK"I~4.ROSE-IO NM1.666E-OS <.947E-09 1.9CIK-IO 1.057E-09 MNM1.582E-OS 1.66RE-O9 1.814K-II O.CC9E10H1.5IVE-OS 4.701E-09 1.883K-09 I.OR<K-09 NHE6.572K-09 R.)30E-09 8.$04E-IO1.96<E-IO NE8.968K-09 R.CSIE-O9 I.IT&K-I9 5.856K10EWE3.003E-OS 8.677E-09 3.400E-09 I.BISE-09 E4.315E-OS I.RI3E-IS 4.C94E09R.<BIE-09 ESE2.837E-OS 7.97)K-09 3.878K-~91.68IE-OO SER.122K-OSC.R5RE-O'9 R.43OE-~I).895K-09 SSE1.073E-OS 3.302E-09 I.RTSEI9C.83RE-IO AREAINt~-2)ATFIXEDISTANCES IHNILES2.503.004.2R9K-IO 2.$9)E-IO4.9RIE-IO 3.367E-IO 3.459E-IO 2.390E-IO I.IS<E-IO 8.260E-II 1.3<9E-IO 9.<ROE-II 8.71)K-IO 1.890E-IO 6.605E"Io4.51<E-IO 6.003E-IO 4.086E-IO 6.146E-IO 4.<RVE-IO 3.172E-IO 2.198E-IO 3.681K-lo 8.527E-IO I.IRBE-09 7.671K-IO 1.53'IE-09 1.037E-09 9'982K-IO6.755E-IO 8.035E-IO 5.169E-IO <.R5IEloR.90IE-IO 4.004.50I594E-Io1.25IE-IO 1.856E-IO ).45<E-)0 1.328E-IO 1.042K-IO 4.638E-II 3.645E-II S.ROBE-II <.)55E-II 1.059E-IO 8.3ISE-II R.<TTE-IO 1.936E-IO 2.236E-IO 1.747K-lo 2.145E-IO 1.91<E-IO 1.22<F.-IO '9.592E-I 'I1.389E-IO 1.084E-IO 1.191E-IO 3.87)E-IO 5.630Elo4.387E-IO 3.667E-IO R.S5TE-IO 2.9'92EIo8.338E-IO 1.596E-IO 1.25)E-IO 3.502.I0IE-10R.<<TE-I01.747E-IO 6.07<E-II6.927K-II 1.389E-IO 3.27<E-IO 2.957E-IO 3.822E-)0 1.609E-IO 1.835E-)0 5.519E-107.172E-I04.867E-103.957E-I0 R.105K"10DPOINTSSYDOLINWIND SECTORS5.00I.OOTE-IO I.ICSE-II8.366K-II 8.932E-)l 3.339K-lI6.682E-II 1.55RE-IO I.<01f-l01.537E-I~7.696E-II S.CTSE-I'I R.619E-103.51OE-I0R.ROTE-III.875E-III.OOCEIo5.508.878E-II 9.5S6E-II C.SSIE-II e.<oef-ll 2.731K-IIS.469E-)l I.R69E-IO 1.1<BE-10I.R59E-II6.29<E-II7.083E-II R.I<IE-10R.SCSE-IO 1.869E-I~1.536E-IO 8.861E-III~~0~0~~IOOI~01~~il~lItDIRKCT)OHFROtlSITE8SSHSl)llSDDDHIJNl)NNllNNNENEKNEfESESfSSE6.006.9)TE-II S.OOIE"II 5.704E-II 8.000E-II 2.27<F.-II 1.5<VE-II1.056E-'10 9.565E-II I.0<BE-II5.23)E-II 5.879E-II I.78IK-IIR.385E-101.555E-III.RBOE-106.903E-II 6.505.999E-II 6.93<E-II 4.963E-II I.749f"'II1.988E-II 3.973E-II 9.127E-II 8.256E-II 9.092E-I) <.SSSE-II 5.083E-II 1.535E-IO 8.050E-IO 1.336E"10 I.IOSE"105.979E-II 7.005.RISE-II C.I8IE"II4.379K-II I.514E-II1.754E-I) 3.505E-I) B.I52E-II7.886E-)I S.IR3E-II4~~IbfII4.<seE-)i 1.35<E-I~I.BOSE-I~I.179K-)O9.75IE-II5.e79E-I) 7.50<.VISE-IIS.119E-II3.896E"II 1.373K-II 1.56IE-II3.)ISE-II 7.)63E-IIC.<83E"II7.139E-II3.573E-II 3.985E-)l I.ROSE-IO 1.60BE-IO I.0<BE"10 8.677K-II <.TOIE-IIDISTANCES 8.004.832E-II <.SBCE-II 3.<92E-II I.23)E-II1.39SE"IIR.794E-II 6.<IVE-II5.81OE-II6.39SE-II 3.80IE-II3.568E-II 1.079K-IO I.<<Of-l09.390E-II 7.776K-II 4.R)6E-II)Ntl)LES8.503.BRIE-II 1.109E-II3.149E-III.IIOE-III.26IK-IIR.5I'9E-IIS.VSSE-II 5.240E-)l 5.770E-II R.BS6E-II 3.el<E-119.788E-II 1.298E-IO 8.16<E-II7.01<E-II 3.80&E-II 9.003.<TOE-II<.OOIE-II R.BS&E-II I.OOTE"11 I.I<<E"112.28<E-II5.2<5E-II 1.753K-ll 5.834E-II 2.616E-IIe.912K-II8.8IBE-III.176E-II7.678E"II 6.3&RE-)l 3.455E-)1 9.503.167K-ll 3.650E"II 2.604K-II9.183K-IR 1.0<RE-IIR.OSRE-II 4.779EII4.333E-II 1.77IE-II2.38<E-II e.&52E-II 8.03<E-II1.072E-106.989E-II 5.799E-II 3.153E-II10.002.904K-ll 3.31<E"II2.384E-II 8.412E-IR 9.5<6E-I2 1.906E-II 4.375E-II 3.968E-II 4.369E"II 8.)822-11 R.125E-II7.352E-II 9.805E-II 6.395E-II 5.31)E-II 2.890E-II IS.001.533E-)l 1.754K-II I.2<RE-II4.393E-IR 4.9&SE-IR 9.907E-)2 2.866E-II R.OCCE-II 8.8'16E-II 1.130EIII.R45E-)l 3.799E11S.054K-II3.30IE-II8.765E-II 1.522E-II eo.oo9.66<E-IR1.099E-II 7.742E-IR e.V<6E-le 3.097E"le 6.168K-le I.105K"II).286K"ll I.4IBE-IIT.OIREIR7.663E-IR 8.35')E-II 3.119E-II8.040E-II I.TRRK-II 9.569E-IR -114-0'$Iqtk~'CI~1tgzt'-"JQ', TABLEC-2D/gTABLE(GRAZINGSEASONMETEOROLOGICAL DATA)HHPUNIT<4ISTACKCORRECTED FOROPEHTERRAINRECIRCULRELAT)VE~tttt1~10~00~I~10ttrO~AT)ONDEPO817)ON PERUN)TAREA)Nil-RfATFIXEDPOINTSBYDOUIIUIHD SECTORS0~~00~~11I~t~~1~OtttOD)RECT)ON FRON81'TE8SSllSUUSUUNUNilHkliNNNENEEHKEESESESSE.50'1.001.079E-OS 3.3e<E-09 ).030K-OS 3.R<RE-O'9 5.999E-09 1.97<K-ot 1.658E-09 5;t39K-10 I.sVRE-09 6.736E-IO <.629E-09 1.579E-~9).586E-OS <.VBRE-~'91.556E-OB <.658E-09 1.63)K-OS 5.076E-09 6.522E-09 2.113E-49 7.276E-09 R.Reef-ot 2.9SSE-OS 8.799K-O'9 3.971E-OB I.1<3E-082.30SE-OS C.595E-09 1.880E-OB 5.557E-49 1.120E-OB 3.3&IE"09 1.54I.RTOE-09 I.RTOE-~9S.47<E-I4R.SRCE-I~R.918E-I~C.CTTE-I~1.90&E"09 I.8ISE-09R.03)f-ot S.BORE-I~9.I<IK-143.<89E-09 <<.CIE-at8,553E-atR.l<3E-09 I.RTTE-49 2.006.7<BE-IO C.B<9E10<<.C<E-IOI.<3RE-I~I.C6RE-I03.7&OE-I4 ).032E-09 9.78SE-IO I.105E-09<.899E-14 5.028E-14 I.BBOK-09 8.375K-ot 1.3538-09 I.138E-09C.7<3E-I~DISTANCES 1NI)ILESR.503.003.50<.)82K-IOR.8<BE-IO 2.06<E-IO <.RSTE-Io 2.93&E-IO R.)36E-)O 2.839E-IO 1.96<E-)0 I.<36E-IO 9.253E-)l 6.<63E-II <.757E-II I.OVSE-'Io 7.5<BE-I'I 5.5&OE-II 2.<ISE-IO 1.683K-IO 1.236K-IO 6.<68E10<<.30E"lo3.217K-IO 6.055E-IO <.129E-Io 2.993E"10 C.953E-IO <.776E-10 3.<TVE-IO 3.IRTE-!0 R.l&VE-IO 1.585E-IO 3.18SE-IO 2.)9<E-IO 1.598E-)0 I.176E-098.036E-)0 5.829E-IO I.<73E-09 I.OOIE-09 7.236EIo$.361K-IO5.672E-IO <.09<K-IO 7.0<5E-IO <.789E-IO 3.<6<E-IO <.16)E-Io 2.82<K-IO 2.0<RE-IO <.001.565E-IO ).622E-IO 1.093K-I~3.63SE-II <.2<9E-II 9.<23E-II 2.<37E-10R.265E-IO e.&39E-lo l.eo&f-lo I.RlefI0<<.IRE-)45.<63EIo3.089EIoR.&Itf-101.5<SE-)0 <.50I.RRTE-IO I.eVef-lo 8.580E-II 2.859E-II 3.3<OE-II 7.39SE-II 1.906E-IO I.77ef-Io2.067E-IO 9.<5)K"II9.<TBE-II 3.<<SE-IO<.263E-IO e.<Iof-Io2.0<BE-IO I.RIOE-IO 5.009.876E-II 1.023E-IO 6.898E-II 8.300E-)l R.&86K-II 5.9<5E-II 1.5RSE-IO 1.<eeE-IO 1.659E-14 7.585EII7.59IE-II2.76<E"lo 3.<I<EIOI.930E-10I.6<<E-10t.TRSE-II 5.50S.)ROE-II 8.<OIE-II 5.65SE-II 1.88&E-II R.ROOE-II <.867E-II I.RSIE-I0 I.I&5E-101.360E-IO 6.205E-II 6.1')9E-Il 2.26)K-I08.798E-IO 1.579K-)4 1.3<TE-IO 7.'993E-II DIRECT)OH FROHSITK8SSllSIII)SUUUHUNUNHll.HHkfNEENEEESKSESSE6.006.796E-)l 7.0)SE-II <.7)RE-III.57IE-II1.830E-II <.0<9E-II I.0<IE"I09.71<E-II1.133K105.158E-II 5.I<6E-II1.882E"10 8.323E-)0 1.31<E-I0I.IR<E-106.68<K-II 6.505.88<EII6.090E-II <.IOSE-II1.375E-II 1.603E"II 3.536E-II 9.007E-II 8.397K-II 9.828K-II <<.9)K-11<<.CRE-II1.627E-IO R.OOIE-IO I.13)E-I~9.702E-II 5.77<K-II 7.0~5.197E-II 5.377K-II 3.CR3E-III.RI<E-'III.<I<EII3.)ROE-II 7.9<TE-II 7.<IIE-II 8.673E-II 3.tCRE-II 3.935E-II I.@35E-I4 I.TCSE-I~'t.tSRK-II 8.56<E-II S.ottf-ll 7.50<.Ceif-Ii <.78TE-II3.22<K)11.080E-II 1.858E-II 8.77&E-II 7.069E-II C.595E-II 7.717E-II 3.52<E-II 3.<99E-II I.eTTE-io I.STOE-148.879K-II 7.622E-II <.5<OE-II D)STANCES 8.00<.153EIf<.29<E-II 8.890E-I) 9.682K-le I.IRTE"II'.<BVE-)l 6.33<E"II 5.91)E-II C.t)TK-II 3.157K"II 3.133E-III.I<<E-I01.<OTE-107.95SE-I) C.833E-II <.473E-ll IHH)LES8.503.750E-II 3.876E-II 8.60TE-)l S.73<K-IR I.0ITK-II2.2<3E-II 5.71)E-fl 5.332K-ll 6.239E-I) R.B<6E-)l 2.823K-ll 1.03IE-10 I.R&SE-IO 7.ITRE-II6.I&5E-II3.677K-ll 9.003.<06f-ll 3.518E-II8.366E-II T.tesf-ie 9.220E-IR 2.03<K-II 5.)TSE-II <.837E-II 5.659E"II 2.580K-II e.ssBE-)l 9.350E-II I.150K-I06.542E-II 5.593K-ll 3.338K-ll 9.503.149E-1I3.210E-II 2.157EII7.2RTE-)8 8.<05E-IR 1.85<E-II <.7)9K-II <<.IIE"II5.164K-ll 2.35)E-II R.370E-II B.seof-ll 1.0<VE-IO 5.985K-II 5.)0IE-II3.0<7K-II 10.002.85)E-)l 8.9<3E-II 1.976E-)f 6.62)E-IR7.698E-)8I.698E-II<.320E-ll <.0<OE-II <.726E-If R.152E"ll8.13)E-II 7.799E-II 9.58TE-II 5.<2<E-II <.673E-)1 R.793E"II )5.001.508E-II 1.5<9E-)l 1.03<K-II 3.<65E-IR <.~IRK-)28.838E-I2R.2<IE-11R.IOSE-fIR.<65f-ll I.I)6E-I)1.097E-II <.0<2E-II <.957E-ll 2.808K-ll e.<<ef-lII.<73E-II20.009.52)f-I29.7<IE-126.<67E-122.)TOEIRR.so<f-le 5.509K-IR 1.392K-I) 1.3)5E-II1.538E-II6.930E-IR 6.766E-IR 2.508E-II 3.069K-lf 1.7<OE-II 1.585E-II t.ecSE-IR -115-F~IFf<<'t<<'FIItC<<<<I TABLEC-3x/q(hHNUALHETEOROLOGICM. 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7.436E-09 9.590K-09 1.45fE-OS 3.292E-DB 3.052K-OB 3.403E"08 2.092E-DB R.RRBE-OB 4.036E-OS 4.501E"082.486K-os I.936K-OB I.225E-OS DISTANCEINNILESe.5oo3.ooo3.500I.I24E-OB I.309E-OB I.IRBE-OS 6.265K-09 B.DOBE-09 I.I92E-OB2.643K-OO 2.445E-OB 2.747E-DB l.706K-OB I.Y92E-OB 3.ROSE"08 3.564E-OS 'I.961K-OSI.544E-OB 9.926E-09 4.000'9.449K09I'92E-089.545E-09 5444E-096.908E-09 I~OOBK-OS2.203E-OS 2.03'IE-08 e.3olE-oa I.44IE-OS I.498E-OB R.644E-DB 2.930E"08 I.CITE-OS I.R75E-088.333K-ot 4.5005.'000S.I44E-09T.ISBE-D'9 9.34BE-O9 S.I66E-09 8.260K-ot 7.276K-ot 4.829E-D9 4.349K"09 6.09IE-09 5.451E-09 B.1I9E"09 1.611E-09 I.885E-DB l.644K-OB I.743K-OB I.SRRE"08 I.97TE-08I.732E-08I.247E-OS I.099E-OB I.RBYE-oa I.leaf-os R.e42f-oa I.942K-os R.477E-OB R.140K-OS I.366K"08 I.I79E-DS I.OSIE-OS '9.365f-ot Y.I73E-09 6.300E-09 5.500C.3885-09 7.244E-09 6.4tYf-093.96IE-094.94SE-09 6.85IE-09 I.457K-08I.35IE-08I.540E-OB 9.8ICE-09 l.004E-OS I.1IOE-08I.SSOE-OS I.035K"08 8.24IE-095.6ITE"09hlttlUALAVERACKSEARINCBSMCMUOMItMtlMIIMtMIMtltttlfNEEttfEEBESE.SOECttl/0IBEC/METER CUBKQl6.0006.5007~Oo~5.765K-09 5.27TK-O'9 4.89'TE-Ot 6.503E-09 5.'923E-09 5.413K-ot 5.863E-09 5.363K-09 4.975K-ot 3.640E-09 3.384E-ot 3.I84K-09 4.5R9E-09 4.l'trf-09 3.939K-09 6.IBIE-09 5.653E-~95.242K-O'9 I.306E-DB I.189E-OS I.DOTE-OS I.RI3K-OS I.I05E-OBI.ORRE-DS l.386E-DS I.265K-.OS I.ITIK-088.86tf-09 S.IRRE-09 7.542K-09 9.039E-09 S.R63E-09 T.CC4K-09 I.525K-OB l.38IE-DB I.RTDKOS1.673E-OS I.5IRE-OS l.38SK-OS 9l99f-098.308E-Ot T.CISE-~97.3442-09 6.644K-ot C.'IDRKOt5.065E-09 4.633E"09 4.Rtlf-ot 7.5004.568E-D9 5.080E-09 4.633K-09 3.005K-O'9 3.708K-D9 4.88IE-09 I.OIBE-DS 9.496E-O'9 I.089K-DS 1.0'33E-0'9 7.I4IE-09l.l74E-OB l.28IE-OS 7.023E-09 S.C33f-o'9 4.004E-09 4.275K-09 4.735K-09 4.330E"09 2.842K-ot 3.500K-O'9 4.562E-D9 9.417K-09 8.859E-09 I.OITE-OB 6.'582K-09 6.68IK-09 l.090K-OS l.lsrf-oa 6.505E-09 5.223K-09 3.744E-09 4.0I4E-09 4.429E-09 4.060E-09 2.695K"09 3.3I2K-09 4.277E-09 8.858E-09 S.R94f-ot 9.526E-09 6.I79E-096.273E-09 I.DICE-08I.ID5E-086.050E-09 4.863K-09 3.5I3E-09 Q!STANCEItltllLESS.DDD8.5009.00D3.780E-09 4.I55E"09 3.BISE-09 2.560K-09 3.I4IE-09 4.022E-09 8.307K-09 7.7'tOE-09 8.953E-09 5.BISE-09 5.908K-09 9.5075-0'I I.O'33E"08 5.648E-09 4.544E-09 3.306E-09 9.5003.570E093.9IOE"09 3CDOE-092.436E"09 2.985E-09 '3.792K-09 Y.BI3E"09 7.338E0'98.437EDt5.493E-09 5.580E-09 8.924E-09 9.CYBE-095.R90E"09 4.P59K093.II9E-09I0.000I5.0003.380E-09 2.269K-O'9 3.C90E-09 R.414E-09 3.403K-09 2.254K092.323E-09 I.C35E092.842E-09 I.983E093.585E-09 2.375E-09 7.368E-D'9 4.SORE096.93IK"09 4.573E-09 7.972E-09 5.210E-09 S.I98E-09 3.474E"09 5.2$4f-ot3.5&6E-09 8.40RE-09 5.4Rtf-09 9.099E-09 5.SIDE"09 4.970E"09 3.I59E-09 4.004E-09 R.S60E-09 R.95IE-09 I.OCOK09eo.oool.689E-09 l.764K-09 1.659K-09 l.e47E-09 I.506E-09 1.748E-09 3.498E-09 3.362E-09 3.876E-09 2.570E-09 2.666E-09 3.950E-09 4.I91E-09R.ersf-ot I.852K-09 I4h7F44 ~~Kxl%tI4~~~a<<gI~~4-lkEJJpII 'j.'ABLEC"3(ANNUALHETEIJROLOGICAL 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