ML17059A424

Rev 14 to Nine Mile Point Nuclear Station Unit 1 Odcm.

ML17059A424
Person / Time
Site:	Nine Mile Point
Issue date:	07/06/1994
From:	ABBOTT R B, TERRY C D NIAGARA MOHAWK POWER CORP.
To:
Shared Package
ML17059A422	List: ML17059A421 ML17059A423 ML17059A424 ML18040A294
References
PROC-940706, NUDOCS 9409020228
Download: ML17059A424 (192)

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NINEMILEPOINTNUCLEARSTATIONNINEMILEPOINTUNIT1OFF-SITEDOSECALCULATION MANUALODCMDATEANDINITIALSAPPROVALS REVISION14R.B.AbbottPlantManagerUnit1C.D.TerryV.P.NuclearEngineering 1INIAGARAMOHAWKPOWERCORPORATION 9409020228 940825PDRADOCK05000220RPDR004152LLUnit1ODCMRevision14June1994

SUMMARYOPREVISIONS PAGERevision14Effective 063094DATElg2gSi6i8i9i1113/1518i21@24i25i3644'749/52-8li86-1163i4i7i10'4'9i20i22'3i263545'6i50'1i8285*29*64,77,78ig19@21@22Ag22Bp124g25@26@112iiiigiii,1216i18'840i4547i52i55i5989i92i93'7129i91-93,953i421@92i95a-c10,16-205J13'8i20'530i65i7966,6916,69February1987December1987January1988May1988(Reissue)

May27,1988(Reissue)

February1990June1990June1992February1993March1993June1993December1993June1994004152LLUnit1ODCMRevision14June1994

ODCM-NINEMILEPOINTUNIT1TABLEOFCONTENTSPacae

2.0 LIQUIDEFFLUENTS

2.1SetpointDeterminations 2.1.1Basis2.1.2ServiceWaterSystemEffluentAlarmSetpoint2.1.3LiquidRadwasteEffluentAlarmSetpoint2.1.4Discussion 2.1;4.1ControlofLiquidEffluentBatchDischarges 2.1.4.2'Simultaneous Discharges ofRadioactive Liquids2.1.4.3SampleRepresentativeness 2.1.4.4LiquidRadwasteSystemOperation 2~1.4.52'ServiceWaterSystemContamination LiquidEffluentConcentration Calculation 2.3DoseDeterminations 2.3.1MaximumDoseEquivalent Pathway3.0GASEOUSEFFL'UENTS 103.1F113.1.23.1.33.1.43.1.53.1.5'3.1.5.23.1.5.3SetpointDeterminations BasisStackMonitorSetpoints Recombiner Discharge (OffGas)MonitorSetpoints Emergency Condenser VentMonitorSetpointDiscussion StackEffluentMonitoring SystemDescription StackSampleFlowPath>>RAGEMSStackSampleFlowPath-OGESMS101010121313131314004152LLUnit1ODCMRevision14June1994

ODCM-NINEMILEPOINTUNIT1TABLEOFCONTENTS(Cont'd)3~15.43.1.5.53.1.5.63'3.2.1-3.2.1.13.2.1.23.2.23.2.2.13.2-2.23.2.2.33'3.44.04.14'4.34.45.05.15.25.3SampleFrequency/Sample AnalysisI-133Estimates GaseousRadwasteTreatment SystemOperation DoseandDoseRateDetermination DoseRateNobleGasesTritium,IodinesandParticulates DoseNobleGasAirDoseTritiumIodinesandParticulates Accumulating DosesCriticalReceptors Refinement ofOffsiteDosesResulting FromEmergency Condenser VentReleases40CFR190REQUIREMENTS Evaluation ofDosesFromLiquidEffluents Evaluation ofDosesFromGaseousEffluents Evaluation ofDosesFromDirectRadiation DosestoMembersofthePublicWithintheSiteBoundaryENVIRONMENTAL MONITORING PROGRAMSamplingStationsInterlaboratory Comparison ProgramCapabilities forThermoluminescent Dosimeters UsedforEnvironmental Measurements Pacae14141515161618191920212122232425262629292930004152LLUnit1ODCMRevision14June1994

ODCM-NINEMILEPOINTUNIT1TABLEOFCONTENTS(Cont'd).

Table1-1Tables2-1to2-8AverageEnergyPerDisintegration AValuesfortheNMP-1FacilityPacae3233Table3-1Table3-2Table3-3CriticalReceptorDispersion Parameters forGroundLevelandElevatedReleasesGammaAirandWholeBodyPlumeShineDoseFactorsforNobleGases(B,andVi)Immersion DoseFactorsforNobleGases414243Tables3-4to3-22Table3>>23Table5.1OrganDoseandDoseRateFactors(Q)Parameters fortheEvaluation ofDosestoRealMembersofthePublicfromGaseousandLiquidEffluents NMP-1Radiological Environmental Monitoring ProgramSamplingLocations 446364Figure5.1-1NineMilePointOn-SiteMapFigure5.1-2NineMilePointOffsiteMapFigure5.1.3-1SiteBoundaries 686970AppendixAAppendixBAppendixCAppendixDLiquidDoseFactorDerivation

(~)PlumeShineDoseFactorDerivation (B(andV))OrganDoseandDoseRateFactorsforIodine-1316133,Particulates andTritium(g)DiagramsofLiquidandGaseousRadwasteTreatment Systems71747888004152LL-iii-Unit1ODCMRevision14June1994

1.0INTRODUCTION

TheOffsiteDoseCalculation Manual(ODCM)providesthemethodology tobeusedfordemonstrating compliance withtheRadiological EffluentTechnical Specifications (RETS),10CFR20,10CFR50,and40CFR190.ThecontentsoftheODCMarebasedonDraftNUREG-0472, Revision3,"Standard Radiological EffluentTechnical Specifications forPressurized WaterReactors,"

September 1982;DraftNUREG-0473, Revision2,"Radiological EffluentTechnical Specifications forBWR's","July1979'UREG 0133,"Preparation ofRadiological EffluentTechnical Specifications forNuclearPowerPlants,"October1978;theseveralRegulatory Guidesreferenced inthesedocuments; and,communication withtheNRCstaff.Section5containsadetaileddescription oftheRadiological Environmental Monitoring (REM)samplinglocations.

Shoulditbenecessary toreviseth'eODCM,theserevisions willbemadeinaccordance withTechnical Specifications.

004152LLUnit1ODCMRevision14June1994

2~02.1.1LIQUIDEFFLUENTS SetpointDeterminations BasisMonitorsetpoints willbeestablished suchthattheconcentration ofradionuclides intheliquideffluentreleasesinthedischarge canalwillnotexceedthoseconcentrations asspecified in10CFR20,AppendixB,TableII,Column2.Setpoints fortheServiceWaterSystemEffluentLinewillbecalculated quarterly basedontheradionuclides identified duringthepreviousyear'sreleasesfromtheliquidradwastesystemortheisotopesidentified inthemostrecentradwastereleaseorotheridentified probablesource.Setpoints fortheLiquidRadwasteEffluentLinewillbebasedontheradionuclides identified ineachbatchofliquidwastepriortoitsrelease.2'~2Afterrelease,theLiquidRadwastemonitorsetpointmayremainasset,orrevertbacktoasetpointbasedonapreviousSemi-Annual Radioactive EffluentReleaseReport,orinstallblankflangeinthedischarge lineanddeclareinoperable inaccordance withthetechnical specification.SincetheServiceWaterSystemeffluentmonitorandLiquidRadwasteeffluentmonitorcanonlydetectgammaradiation, thealarmsetpoints arecalculated byusingtheconcentration ofgammaemittingisotopesonly(orthecorresponding MPCvaluesforthesameisotopes, whichever arehigher)intheE<(pCi/ml)+

expression (Section2.1.2,2.1.3).TheRequiredDilutionFactoriscalculated usingconcentrations ofallisotopespresent(orthecorresponding MPCvaluesforthesameisotopes, whichever arehigher)including tritiumandothernon-gamma emitterstoensurethatallradionuclides inthedischarge canaldonotexceed10CFR20limits.ServiceHaterSystemEffluentLineAlarmSetpointThedetailedmethodsforestablishing setpoints fortheServiceWaterSystemEffluentLineMonitorshallbecontained intheNineMilePointStationProcedures.

Thesemethodsshallbeinaccordance withthefollowing:

Setpoint(Hialarm)<0.9ZCimlCFTDFF[(pCi/ml)n MPC,]I+background Setpoint(Alertalarm)<0.7ZCiml.CFTDFF+background

[(pCml)zMPC,]l(pCi/ml)>(pCi/ml)nTDFconcentration ofgammaemittingisotopeiinthesample,orthecorresponding MPCofgammaemittingisotopei(MPC)whichever ishigher(units~pCi/ml).concentration ofanyradioactive isotopeiinthesampleincluding tritiumandothernon-gamma emittersorcorresponding MPCofisotopei,MPCwhichever ishigher(units~pCi/ml).TotalDilutionFlow(units=gallons/minutes).

ServiceWaterFlow(units=gallons/minutes).

004152LLUnit1ODCMRevision14June1994

2.1~2ServiceWaterSystemEffluentLineAlarmSetpoint(Cont'd)CFMPHSample(MPC)Nmonitorcalibration factor(units=netcpm/pCi/ml

).liquideffluentradioactivity concentrations limitforradionuclide iasspecified in10CFR20,AppendixB,TableII,Column2.ThosenuclidespresentinthepreviousbatchreleasefromtheliquidradwasteeffluentsystemorthosenuclidespresentinthelastSemi-annual Radioactive EffluentReleaseReport(units=pCi/ml)orthosenuclidespresentintheservicewatersystem.**

sameasMPC,butforgammaemittingnuclidesonly.0.9and0.7factorsofconservatism toaccountforinaccuracies.

Z~[(pCi/ml)z/MPC,)=RequiredDilutionFactor.IfMPCvaluesareusedinthe(pCi/ml)+,

theymustalsobeusedincalculating RDF(numerator).

TDF/F~ActualDilutionFactor2,1.3LiquidRadwasteEffluentLineAlarmSetpointThedetailedmethodsforestablishing setpoints fortheLiquidRadwasteEffluentLineMonitorshallbecontained intheNineMilePointStationProcedures.

Thesemethodsshallbeinaccordance withthefollowing:

EIf(pCi/ml)n'/MPCi)(pCi/ml)+E/[(pCi/ml)n/MPC()concentration ofgammaemittingisotopeiinthesampleorthecorresponding MPCofgammaemittingisotopei,(MPC),whichever ishigher.(pCi/mlTDFCFconcentration ofanyradioactive isotopeiinthesampleincluding tritiumandothernon-gamma emittersorthecorresponding MPCofisotopeiMPC,whichever ishigher.(unitspCi/ml).TotalDilutionFlow(units=gallons/minutes).

RadwasteEffluentFlow(units=gallons/minutes).

monitorcalibration factor(units=netcps/pCi/ml).

• • ForperiodswithknownreactorwatertoRCLCsystemleakage,RCLCmaximumpermissible concentration maybeprudently substituted fortheabove.Unit1ODCMRevision14-3-June1994

2'~3LiquidRadwasteEffluentLineAlarmSetpoint(Cont'd)MPC<(MPC)I0.9and0.7liquideffluentradioactivity concentration limitforradionuclide iasspecified in10CFR20,AppendixB,TableII,Column2,forthosenuclidesdetectedbyspectralanalysisofthecontentsoftheradwastetankstobereleased.

(units=pCi/ml)sameasMPC,butforgammaemittingnuclideonly.factorsofconservatism toaccountforinaccuracies.

E[(pCi/ml)z/MPC,]

=RequiredDilutionFactor.IfMPCvaluesareusedinthe(pCi/ml),

theymustalsobeusedincalculating RDF(numerator).

Notes:(a)IfTDF/FZ,[(pCi/ml)n/MPC;)

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

Thiswillalsoresultinadischarge canalconcentration atapproximately 50%maximumpermissible concentration.

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

2.1.4Discussion 2'.F1ControlofLiquidEffluentBatchDischarges AtNineMilePointUnit1LiquidRadwasteEffluents arereleasedonlyonabatchmode.Topreventtheinadvertent releaseofanyliquidradwasteeffluents, radwastedischarge ismechanically isolated(blankflangeinstalled ordi.scharge valvechain-locked closed)following thecompletion ofabatchreleaseorseriesofbatchreleases.

2.1.4.2Thismechanical isolation remainsinplaceandwillonlyberemovedpriortothenextseriesofliquidradwastedischarges afterallanalysesrequiredinstationprocedures andTechnical Specification Table4.6.15-1A areperformed andmonitorsetpoints havebeenproperlyadjusted.

Simultaneous Discharges ofRadioactive Liquids.Ifduringthedischarge ofanyliquidradwastebatch,thereisanindication thattheservicewatercanalhasbecomecontaminated (throughaservicewatermonitoralarmorthroughagrabsampleanalysisintheeventthattheservicewatermonitorisinoperable) thedischarge shallbeterminated immediately.

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

limitsarenotexceeded.

004152LLUnit1ODCMRevision14June1994

2.1.4.2Simultaneous Discharges ofRadioactive Liquids(Cont'd)Inaccordance withSiteChemistry procedures, controlsareinplacetoprecludeasimultaneous releaseofliquidradwastebatchtanks.Inaddition, anindependent verification ofthedischarge valveline-upisperformed priortodischarge toensurethatsimultaneous discharges areprevented.

2'.4.3SamplingRepresentativeness ThissectioncoversTechnical Specification Table4.6.15-1Notebconcerning thoroughly mixingofeachbatchofliquidradwastepriortosampling.

LiquidRadwasteTanksscheduled fordischarge atNineMilePointUnit1areisolated(i.e.inletva'ivesmarkedup)andatleasttwotankvolumesofentrained fluidsarerecirculated priortosampling.

Minimumrecirculation timeiscalculated asfollows:MinimumRecirculation Time~2.0(T/R)Where:2'.4.4~~~2.0=Plantestablished mixingfactor,unitlessTTankvolume',galR~Recirculation flowrate,gpmAdditionally, theHi,AlarmsetpointoftheLiquidRadwasteEffluentRadiation Monitorissetatavaluecorresponding tonotmorethan70%ofitscalculated responsetothegrabsampleorcorresponding MPCvalues.Thus,thisradiation monitorwillalarmifthegrabsample,orcorresponding MPCvalue,issignificantly lowerinactivitythananypartofthetankcontentsbeingdischarged.

LiquidRadwasteSystemsOperation Technical Specification 3.6.16.arequiresthattheliquidradwastesystemshallbeusedtoreducetheradioactive materials inliquidwastespriortotheirdischarge, 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 inSection2.3ofthismanualpriortothe.releaseofeachbatchofliquidwaste.Thissamedoseprojection ofSection2.3willalsobeperformed intheeventthatuntreated liquidwasteisdischarged, toensurethatthedoselimitsofTechnical Specification 3.6.15.a(2) arenotexceeded.

(Therebyimplementing therequirements of10CFR50.36a, GeneralDesignCriteria60ofAppendixAandtheDesignObjective giveninSectionII-DofAppendixIto10CFRSO).004152LLUnit1ODCMRevision14June1994

2'.4'LiquidRadwasteSystemsOperation (Cont'd)Forthepurposeofdoseprojection, thefollowing assumptions shallbemadewithregardtoconcentrations ofnon-gamma emitting~radionuclides subsequently analyzedoff-site:

a)[H-3]6H-3Concentration foundrecentcondensate storagetankanalysisb)[Sr-89]S4xCs-137Concentration c)[Sr-90]s0.5xCs-137Concentration 2~1~4.5d)[Fe-55]s1xCo-60Concentration AssumedScalingFactorsusedinb,c,anddaboverepresent conservative estimates derivedfromanalysisofhistorical datafromprocesswas'testreams.Following receiptofoff-siteH-3,Sr-89,Sr-90andFe-55analysisinformation, doseestimates shallberevisedusingactualradionuclide concentrations andactualtankvolumesdischarged.

ServiceWaterSystemContamination Servicewaterisnormallynon-radioactive.

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

Ifitisdetermined thataninadvertent radioactive discharge isoccurring fromtheservicewatersystem,then:a)A50.59safetyevaluation shallbeperformed (ref.IGEBulletin80-10)ib)dailyservicewatereffluentsamplesshallbetakenandanalyzedforprincipal gammaemittersuntilthereleaseisterminated, 2~2c)anincidentcomposite shallbepreparedforH-3,grossalpha,Sr-89,Sr-90andFe-55analysesand,d)doseprojections shallbeperformed inaccordance withSection2.3ofthismanual(usingestimated concentrations forH-3,Sr-89,Sr-90andFe-55tobeconservatively determined bysupervision atthetimeoftheincident).

Additionally, servicewatereffluentmonitorsetpoints mayberecalculated usingtheactualdistribution ofisotopesfoundfromsampleanalysis.

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

004152LLUnit1ODCMRevision14June1994

2'LiquidEffluentConcentration Calculation (Cont'd)Theconcentration ofradioactivity fromLiquidRadwastebatchreleasesand,ifapplicable, ServiceWaterSystemandemergency condenser start<<upventdischarges areincludedinthecalculation.

Thecalculation isperformed foraspecificperiodoftime.Nocredittakenforaveraging overthecalendaryearaspermitted by10CFR20.106.

Thelimitingconcentration iscalculated asfollows:MPCFraction=E~[(E,CF,)/(MPC)

E,F,))Where:MPCFractionThelimitingconcentration of10CFR20,AppendixB,TableII,forradionuclides otherthandissolved orentrained noblegases..Fornoblegases,theconcentration shallbelimitedto2E-4microcurie/ml totalactivity.

C.=(pCi/ml)

~Theconcentration ofnuclideiinparticular effluentstreams,pCi/ml.F,MPCiTheflowrateofaparticular effluentstreams,gpmoThelimitingconcentration ofaspecificnuclideifrom10CFR20,AppendixB,TableII,Column2(noblegaslimitis2E-4pCi/ml).Z,(pCi/ml)>F,)

=Thetotalactivityrateofnuclidei,inalleffluentstreamss.Z,(F,)PThetotalflowrateofalleffluentstreamss,gpm(including thosestreamswhichdonotcontainradioactivity).

2.32~3~1AvalueoflessthanoneforMPCfractionisconsidered acceptable forcompliance withTechnical Specification Section3.6.15.a.(1).

DoseDetermination MaximumDoseEquivalent PathwayAdoseassessment reportwaspreparedfortheNineMilePointUnit1facilitybyCharlesT.Main,Inc.,ofBostoniMAThis.reportpresented thecalculated doseequivalent ratestoindividuals aswellasthepopulation withina50-mileradiusofthefacilitybasedontheradionuclides releasedinliquidandgaseouseffluents duringthetimeperiodsof1July1980through31December1980andfromJanuary1981through31December1981.Theradwasteliquidreleasesarebasedonacanaldischarge rateof590ft~/secwhichaffectsnearfieldandfarfielddilutiony therefore, thisreportisspecifictothissituation.

Utilizing theeffluentdatacontained intheSemi-Annual Radioactive EffluentReleaseReportsassourceterms,doseequivalent ratesweredetermined usingtheenvironmental pathwaymodelsspecified inRegulatory Guides1.109and1.111asincorporated intheNRCcomputercodesLADTAPfor.liquidpathways, andXOQDOQandGASPARforgaseouseffluentpathways.

Doseequivalent rateswerecalculated forthetotalbodyaswellassevenorgansand/ortissuesfortheadult,teen,child,andinfantagegroups.Fromthestandpoint ofliquideffluents, thepathwaysevaluated includedfishanddrinkingwateringestion, andexternalexposuretowaterandsediment.

004152LLUnit1ODCMRevision14June1994

2.3.1MaximumDoseEquivalent Pathway(Cont'd)Themajorityofthedoseforaradwasteliquidbatchreleasewasreceivedviathefishpathway.However,tocomplywithTechnical Specifications fordoseprojections, thedrinkingwaterandsedimentpathwaysareincluded.

Therefore, alldosesdueto.liquideffluents arecalculated monthlyforthefishanddrinkingwateringestion pathwaysandthesedimentexternalpathwayfromalldetectednuclidesinliquideffluents releasedtotheunrestricted areastoeachorgan.Thedoseprojection forliquidbatchreleaseswillalsoincludedischarges fromtheemergency condenser ventasapplicable, forallpathways.

Eachagegroupdosefactor,~,isgiveninTables1-1to1-8.Toexpeditetimethedoseiscalculated foramaximumindividual insteadofeachagegroup.Thismaximumindividual willbeacomposite ofthehighestdosefactorofeachagegroupforeach'organ, henceA.Thefollowing expression fromNUREG0133,Section4.3isusedtocalculate dose:Di=Zi(245t.(hTgCgFg)

)Where:D,Thecumulative dosecommitment tothetotalbodyoranyorgan,fromtheliquideffluents forthetotaltimeperiod(dT),mrem.hT,=ThelengthoftheLthtimeperiodoverwhichCzandFzareaveragedforallliquidreleases, hours.C~~Theaverageconcentration ofradionuclide, i,inundiluted liquideffluents duringtimeperiodhTfromanyliquidrelease,pCi/ml.FThesiterelatedingestion dosecommitment factortothetotalbodyoranyorgantforeachidentified principal gammaorbetaemitterforamaximumindividual, mrem/hrperpCi/ml.ThenearfieldaveragedilutionfactorforC~duringanyliquideffluentrelease.Definedastheratioofthemaximumundiluted liquidwasteflowduringreleasetotheaverageflowfromthesitedischarge structure tounrestricted receiving waters,unitless.

Avaluesforradwasteliquidbatchreleasesata"discharge rateof295ft~/sec(onecirculating waterpumpinoperation) arepresented intablesl-lto1-4.Avaluesforanemergency condenser ventreleasearepresented intables1-5to1-8.Theemergency condenser ventreleasesareassumedtotraveltotheperimeter drainsystemandreleasedfromthedischarge structure atarateof.33ft~/sec.SeeAppendixAforthedosefactorA,derivation.

To.expedite timethedoseiscalculated toamaximumindividual.

Thismaximumindividual isacomposite ofthehighestdosefactorAofeachagegroupaforeachorgantandeachnuclidei.Ifanuclideisdetectedforwhichafactorisnotlisted,thenitwillbecalculated andincludedinarevisiontotheODCM.Alldosescalculated inthismannerforeachbatchofliquideffluentwillbesummedforcomparison withquarterly andannuallimits,addedtothedosesaccumulated fromotherreleasesinthequarterandyearofinterest.

Inallcases,thefollowing relationships willholds004152LLUnit1ODCMRevision14June1994

2~3.1MaximumDoseEquivalent Pathway(Cont'd)Foracalendarquarter:D,<1.5mremtotalbodyD,<5mremforanyorganForthecalendaryear:D,<3.0mremtotalbodyD,<10mremforanyorganWhere:D,totaldosereceivedtothetotalbodyoranyorganduetoliquideffluentreleases.

Iftheselimitsareexceeded, aspecialreportwillbesubmitted totheNRCidentifying thecauseandproposedcorrective actions.Inaddition, iftheselimitsareexceededbyafactoroftwo,calculations shallbemadetodetermine ifthedoselimitscontained in40CFR190havebeenexceeded.

Doselimits,ascontained in40CFR190aretotalbodyandorgandosesof25mremperyearandathyroiddoseof75mremperyear.Thesecalculations willincludedosesasaresultofliquidandgaseouspathwaysaswellasdosesfromdirectradiation.

Theliquidpathwayanalysiswillonlyincludethefishandsedimentpathwayssincethedrinkingwaterpathwayisinsignificant.

Thispathwayisonlyincludedinthestation's effluentdoseprojections tocomplywithTechnical Specifications.

Liquid,gaseousanddirectradiation pathwaydoseswillconsidertheJamesA.FitzPatrick andNineMilePointUnitIIfacilities aswellasNineMilePointUnitINuclearStation.Intheeventthecalculations demonstrate thatthe40CFR190doselimits,asdefinedabove,havebeenexceeded, thenareportshallbepreparedandsubmitted totheCommission within30daysasspecified inSection3.6.15.doftheTechnical Specifications.

Section4.0oftheODCMcontainsmoreinformation concerning calculations foranevaluation ofwhether40CFR190limitshavebeenexceeded.

004152LLUnit1ODCMRevision14June1994

GASEOUSEFFLUENTS SetpointDeterminations BasisStackgasandoffgasmonitorsetpoints willbeestablished suchthattheinstantaneous releaserateofradioactive materials ingaseouseffluents doesnotexceedthe10CFR20limitsforannualreleaserate.Thesetpoints willbeactivated iftheinstantaneous doserateatorbeyondthe(land)siteboundarywouldexceed500mrem/yrtothewholebodyor3000mrem/yr.to theskinfromthecontinuous releaseofradioactive noblegasinthegaseouseffluent.

Emergency condenser ventmonitorsetpoints willbeestablished suchthatthereleaserateforradioactive materials ingaseouseffluents donotexceedthe10CFR20limits.forannualreleaserateovertheprojected longestperiodofrelease.Monitorsetpoints fromcontinuous releasepointswillbedetermined onceperquarterundernormalreleaserateconditions andwillbebasedontheisotopiccomposition oftheactualreleaseinprogress, oranoffgasisotopicdistribution oramoreconservative defaultcomposition specified inthepertinent procedure.

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

Underabnormalsitereleaserateconditions, mo'nitoralarmsetpoints fromcontinuous releasepointswillberecalculated and,ifnecessary, resetatmorefrequentintervals asdeemednecessary byCORMSupervision.

Inparticular, contributions frombothJAFandNMP-2andtheEmergency Condenser Ventsshallbeassessed.

JDuringoutagesanduntilpoweroperation isagainrealized, thelastoperating stackandoffgasmonitoralarmsetpoints shallbeUsedeSincemonitorsrespondtonoblegasesonly,monitoralarmpointsaresettoalarmpriortoexceeding thecorresponding totalbodydoserates.3'.2Theskindoseratelimitisnotusedinsetpointcalculations becauseitisneverlimiting.

StackMonitorSetpoints Thedetailedmethodsforestablishing setpoints shallbecontained inthestationprocedures.

Thesemethodsshallapplythefollowing generalcriteria:

(1)Rationale forStackmonitorsettingsisbasedonthegeneralequation:

releaserateactual=releaseatemax.allowable corresp.doserate,actualcorresp.doserate,max.allowable Z..lQi(VI+(SF)

I(~/9)~)500mrem/yr004152LL-10-Unit1ODCMRevision14June1994

3.1.2StackMonitorSetpoints (Cont'd)~~~Where:kQ<releaserateforeachisotopei,pCi/sec.V(gammawholebodydosefactorinunitsofmrem/yrperpCi/sec.(SeeTable3-2).instantaneous releaseratelimitpCi/sec.(2)(3)(4)Toensurethat10CFR20andTechnical Specifications doseratelimitsarenotexceeded, theHiHialarmsonthestackmonitorsshallbesetlowerthanorequalto(0.9)(Q).Hialarmsshallbesetlowerthanorequalto(0.5)(Q)Basedontheaboveconservatism, thedosecontribution fromJAFandNMP-2canusuallybeignored.DuringEmergency Classifications atJAForNMP-2duetoairborneeffluent, orafteremergency condenser ventreleasesofsignificant proportions, the500mrem/yrvaluemaybereducedaccordingly.

ToconvertmonitorgrosscountratestopCi/secreleaserates,thefollowing general'formula shallbeapplied:(C-B)K,=Q=pCi/sec,releaserateWhere:CBK,monitorgrosscountrateincpsorcpmmonitorbackground countratestackmonitorefficiency factorwithunitsofpCi/sec-cps orpCi/sec-cpm (5)MonitorK,factorsshallbedetermined usingthegeneralformulasK,=E,Q;/(C-B)Where:Q,=individual radionuclide stackeffluentreleaserateasdetermined byisotopicanalysis.

K,factorsmoreconservative thanthosecalculated bytheabovemethodology maybeassumed.Alternatively, whenstackreleaseratesarenearthelowerlimitofdetection, thefollowing generalformulamaybeusedtocalculate k,:1/K,~E=EFZY3.E4daffSec.-pCiWhere:f=stackflowincc/sec.E=efficiency inunitsofcpm-cc/pCi orcps-cc/pCi (cpm=countsperminute;cps=countspersecond).E=cpm-cc/bps orcps-cc/@ps.

Fromenergycalibration curveproducedduringNISTtraceable primarygascalibration ortransfersourcecalibration (bps~betapersecond;@ps=gammaspersecond).004152LLUnit1ODCMRevision14June1994

3.1+2StackMonitorSetpoints (Cont'd)Yg=b/d(betas/disintegration) orY/d(gammas/disintegration).

F,Activityfractionofnuclideiinthemixture.i~nuclidecounter.k=discreteenergybetaorgammaemitterpernuclidecounter.s=seconds.Thismonitorcalibration methodassumesanoblegasdistribution typicalofarecoilreleasemechanism.

Toensure'thatthecalculated efficiency isconservative, betaorgammaemissions whoseenergyisabovetherangeofcalibration ofthedetectorarenotincludedinthecalculation.

3.1.3Recombiner Discharge (OffGas)MonitorSetpoints (1)TheHi-Hialarmpointsshallactivatewithrecombiner discharge ratesequaltoorlessthan500,000pCi/sec.Thisalarmpointmaybesetequaltoorlessthan1Ci/secforaperiodoftimenottoexceed60daysprovidedtheoffgastreatment systemisinoperation.

(2)TheHialarmpointsshallactivatewithrecombiner discharge ratesequaltoorlessthan500,000pCi/sec.According totheUnit1Technical Specifications, Note(C)toTable4.6.14-2, thechannelfunctional testofthecondenser airejectorradioactivity monitorshalldemonstrate thatautomatic isolation ofthispathwayoccursifeitherofthefollowing conditions exist:i)Instruments indicatetwochannelsabovetheHi>>Hialarmsetpoint, ii)Instruments indicateonechannelaboveHi-Hialarmsetpointandonechanneldownscale.

Thisautomatic isolation functionistestedonceperoperating cycleinaccordance withstationprocedures.

(3)ToconvertmonitormR/hrreadingstopCi/sec,theformulabelowshallbeapplied:(R)(K)=QpCi/sec recombiner discharge releaserateWhere:R=mR/hrmonitorindicator.

Kgefficiency factorinunitsofpCi/sec/mR/hr determined priortosettingmonitoralarmpoints.(4)MonitorKRfactorsshallbedetermined usingthegeneralformula:KR=E)Q;/RWhere:Q,=individual radionuclide recombiner discharge releaserateasdetermined byisotopicanalysisandflowratemonitor.Kfactorsmoreconservative thanthosecalculated bytheabovemethodology maybeassumed.004152LL-12-Unit1ODCMRevision14June1994

3.1o3Recombiner Discharge (OffGas)MonitorSetpoints (Cont'd)(5)Thesetpoints chosenprovideassurance thatthetotalbodyexposuretoanindividual attheexclusion areaboundarywillnotexceedaverysmallfractionofthelimitsof10CFRPart100intheeventthiseffluentisinadvertently discharged directlytotheenvironment withouttreatment (therebyimplementing therequirements ofGeneralDesignCriteria60and64ofAppendixAto10CFRPart50).Additionally, thesesetpoints servetolimitbuildupoffissionproductactivitywithinthestationsystemswhichwouldresultifhighfuelleakageweretobepermitted overextendedperiods.3~1~4Emergency Condenser VentMonitorSetpointThemonitorsetpointwasestablished bycalculation

("Emergency Condenser VentMonitorAlarmSetpoint",

January13,1986,NMPCFileCodef16199).Assumingahypothetical casewith(1)reactorwateriodineconcentrations higherthantheTechnical Specification Limit,(2)reactorwaternoblegasconcentrations higherthanwouldbeexpectedatTechnical Specification iodinelevels,and(3)leakageofreactorsteamintotheemergency condenser shellat300%ofratedflow(or1.3E6lbs/hr),thecalculation predictsanemergency condenser ventmonitorresponseof20mR/hr.Suchareleasewouldresultinlessthan10CFR20doseratevaluesatthesiteboundaryandbeyondfortypicalemergency condenser cooldownperiods.Sincea20mR/hrmonitorresponsecan,intheory,beachievable onlywhenreactorwateriodinesarehigherthanpermitted byTechnical Specifications, aconservative monitorsetpointof5mr/hrhasbeenadopted.3.1~5~~3.1~5.1Discussion StackEffluentMonitoring SystemDescription TheNMP-1StackEffluentMonitoring Systemconsistsoftwosubsystems; theRadioactive GaseousEffluentMonitoring System(RAGEMS)andtheoldGeneralElectricStackMonitoring System(OGESMS).

Duringnormaloperation, theOGESMSshallbeusedtomonitorstationnoblegaseffluents andcollectparticulates andiodinesamplesincompliance withTechnical Specification requirements.

TheRAGEMSisdesignedtobepromptlyactivated fromtheMainControlRoomforuseinhighrangemonitoring duringaccidentsituations incompliance withNUREG0737criteria.

Overallsystemschematic fortheOGESMSandRAGEMSareshownonFigureB-9.Asimplified viewofRAGEMSShowingUnit0,1,2,3and4canbefoundonFigureB-8.TheRAGEMScanprovidecontinuous accidentmonitoring andon-lineisotopicanalysisofNMP-1stackeffluentnoblegasesatLowerLevelsofDetection lessthanTechnical Specification Table4.6.15-2limits.Activities aslowas5.0E-8andashighas2.0E5pCi/ccfornoblegasesaredetectable bythesystem.3'.52StackSampleFlowPath-RAGEMSTheeffluentsampleisobtainedinsidethestackatelevation 530'singanisokinetic probewithfourorifices.

Thesamplelinethenbendsradiallyoutandbackintothestack;descendsdownthestackandoutofthestackatapproximately elevation 257';runshorizontally (enclosed inheattracing)some270'longtheoffgastunnel;andenterstheRAGEMSlocatedontheTurbineBuilding250'Dilution cabinet-Unit0)andOffGasBuilding247'Particulate, Iodine,NobleGasstations-Units1-3).004152LL-13-Unit1ODCMRevision14June1994

StackSampleFlowPath-RAGEMS(Cont'd)IntheDilutioncabinetofthe'RAGEMS, thestackgasmaybedilutedduringaccidentsi.tuations approximately 100-200X(firststage)or10000-40000 X(firstandsecondstage)withgaseousni.trogen suppliedfromanon-si.teliquidnitrogenstoragetank(seeFigureB-9).FromUnit0,thesamplegasentersUnit1-3ofRAGEMSandflowsthruin-lineparticulate andiodinecartridges andthenthrueithera6liter(lowrange)or30cc(high.range)noblegaschamber.ThesamplegasnextflowsbackthruUnit0andtheoffgastunnel;andbackintothestack.3StackSampleFlowPath-OGESMSTheOGESMSsampleisobtainedfromthesamestacksampleprobeastheRAGEMS.Fromtheexitofthestackatelevation 257',thesamplelinerunseastapproximately 20'ndthenvertically approximately 8'otheOGESMSskid.IntheOGESMS,sampleflowsthruaparticulate/iodi.ne cartridge housingandfournoblegasscintillation detectors (i.e.,07and08lowrangebetadetectors andRN-03AandRN-03Bhighrangegammadetectors).

FromOGESMS,thestacksampleflowsbackintothestackatapproximately elevation 257'.3.1~5'~~~3'o5~5AllOGESMSdetectoroutputsaremonitored andrecordedremotelyintheMainControlRoom.Alarmingcapabilities areprovidedtoalertOperators ofhighreleaserateconditi.ons priortoexceeding Technical Speci.fication 3.6.15.b(1)adoseratelimits.Stackparticulate andiodinesamplesareretrieved manuallyfromtheOGESMSandanalyzedinthelaboratory usinggammaspectroscopy atfrequencies andLLDsspecified inTable4.6.15-2oftheTechnical Specifications.

SamplingFrequency/Sample AnalysisRegardless ofwhichstackmonitoring subsystem isutili.zed, radioactive gaseouswastesshallbesampledandanalyzedinaccordance 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, followi.ng startup,shutdownandinconjunction witheachdrywellpurge.Consistent withTechnical Specification Table4.6.15-2, stackeffluenttritiumis'sampledmonthly,duringeachdrywellpurge,andweeklywhenfuelisoffloadeduntilstablereleaseratesaredemonstrated.

Samplesareanalyzedoff-site.

Linelosscorrection factorsareappliedtoallparticulate andiodineresults.Correction factorsof2.0and1.5areusedfordataobtainedfromRAGEMSandOGESMSrespectively.

Thesecorrection factorsarebasedonempirical datafromsamplingconducted atNMP-1i.n1985(memofromJ.BlasiaktoRAGEMSFile,1/6/86,"StackSampleRepresentativeness Study:RAGEMSversusIn-StackAuxiliary ProbeSamples").I-133Estimates Monthly,thestackeffluentshallbesampledforiodinesover'24hourperiodandtheI-135/I-131 andtheI-133/I-131 ratioscalculated.

Theseratiosshallbeusedtocalculate I-133,I-135releaseforlongeracquisition samplescollected duringthemonth.004152LL-14-Unit1ODCMRevi.sion 14June1994

3.1.5'3~1.5~6I-133Estimates (Cont'd)Additionally, theI-135/I-131 andI-133/I-131 ratiosshouldalsobedetermined afterasignificant changeintheratioissuspected (eg,plantstatuschangesfromprolonged shutdowntopoweroperation orfueldamagehasoccurred).

GaseousRadwasteTreatment 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 withregardtoreleaseratesofnon-gamma emittingradionuclides subsequently analyzedoff-site:

a)H-3releaserate54pCi/secb)Sr>>89releaserate.'54xCs-137releaseratec)Sr-90releaserateS0.5xCs-137releaserated)Fe-55releaserateS1xCo-60releaserateAssumedreleaseratesrepresent conservative estimates derivedfromanalysisofhistorical datafromeffluentreleasesandprocesswastestreams(SeeNMP34023,C.WaretoJ.Blasiak,April29,1988,"DoseEstimates forBeta-Emitting Isotopes"

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

DoseandDoseRateDeterminations Inaccordance withspecifications 4.6.15.b.(1),

4.6.15.b.(2),

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

(1)TotalbodydoseratesandgammaairdosesatthemaximumX/Qlandsectorsiteboundaryinterface andbeyond.(2)SkindoseratesandbetaairdosesatthemaximumX/Qlandsectorsiteboundaryinterface andbeyond.(3)ThecriticalorgandoseanddoserateatthemaximumX/Qlandsectorsiteboundaryinterface andatacriticalreceptorlocationbeyondthesiteboundary.

Averagemeteorological data(ie,maximumfiveyearannualaverageX/QandD/Qvaluesinthecaseofelevatedreleasesor1985annualaverageX/QandD/Qvalues,inthecaseofgroundlevelreleases) shallbeutilizedfordoseanddoseratecalculations.

Whereaveragemeteorological dataisassumed,doseanddoseratesduetonoblegasesatlocations beyondthesiteboundarywillbelowerthanequivalent siteboundarydoseanddoserates.Therefore, undertheseconditions, calculations ofnoblegasdoseanddoseratesbeyondthemaximumX/Qlandsectorsiteboundarylocations canbeneglected.

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

004152LL-15-Unit1ODCMRevision14June1994

DoseandDoseRateDeterminations (Cont'd)Emergency condenser ventreleasecontributions tothemonthlydoseanddoseratedeterminations willbeconsidered onlywhentheemergency condenser returnisolation valveshavebeenopenedforreactorcooldown, ifEmergency Condenser tubeleaksdevelopwithorwithoutthesystem'sreturnisolation valveopened,orifsignificant activityisdetectedintheEmergency Condenser Shell.Withouttubeleakagedosecontributions fromemergency condenser ventreleasesaretobedetermined basedoncondensate storagetankandemergency condenser shellisotopicdistributions.

Whenreleasesfromtheemergency condenser haveoccurred, doserateanddosedeterminations shallbeperformed usingmethodology in3.2.1and3.2.2.Furthermore, environmental samplingmayalsobeinitiated torefineanyactualcontribution todoses.SeeSection3.4.Criticalorgandosesanddoseratesmay,beconservatively calculated byassumingtheexistence ofamaximumindividual.

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

TocomplywithTechnical Specifications wewillcalculate themaximumindividual doserateatthesiteboundaryandbeyondatthecriticalresidence.

3~2~1Ifdoseordoseratescalculated, usingtheassumptions notedabove,reachTechnical Specification limits,actualpathwayswillbeevaluatedi anddose/dose ratesshallbecalculated atseparatecriticalreceptorlocations andcomparedwithapplicable limits.DoseRateDoserateswillbecalculated monthly,ataminimum,orwhentheHi-Histackmonitoralarmsetpointisreached,todemonstrate thatdoseratesresulting fromthereleaseofnoblegases,tritium,iodines,andparticulates withhalflivesgreaterthan8daysarewithinthelimitsspecified in10CFR.20.

These'limits are:NobleGasesWholeBodyDoseRate:500mrem/yrSkinDoseRate:3000mrem/yr3.21.1TritiumIodinesandParticulates OrganDoseRate:1500mrem/yrNobleGasesThefollowing noblegasdoserateequationincludesthecontribution fromthestack(s)elevatedreleaseandtheemergency condenser vent(v)groundlevelreleasewhenapplicable (Seesection3.2).Toensurethatthesitenoblegasdoseratelimitsarenotexceeded, thefollowing procedural actionsaretakeniftheoffsitedoseratesfromUnit1exceed10%ofthelimits:1)NotifytheUnit1SSS(StationShiftSupervisor) andUnit1Supervisor Chemistry.

004152LL-16-Unit1ODCMRevision14June1994

3.2.1.1NobleGases(Cont'd)2)NotifytheUnit2SSSandUnit2Supervisor Chemistry andrequesttheUnit2contribution tooffsitedose.3)NotifytheSSSoftheJamesA.Fitzpatrick NuclearPlantandrequesttheFitzpatrick contribution tooffsitedose.4)Increasethefrequency ofperforming noblegasdosecalculations, ifnecessary, toensureSite(NineMilePointUnits1and2andFitzpatrick) limitsarenotexceeded.

Additionally, alarmsetpoints aresetat50%ofthedoseratelimittoensurethatsitelimitsarenotexceeded.

ThisalarmsetpointisadjustedifthenoblegasdoseratefromUnit1isgreaterthan10%ofthelimit.Fortotalbodydoserates(mrem/sec):

DR(mrem/sec)

=3.17E-SZ)[(V~

+(SF)Q(X/Q)

~)Q+(SF)Q(X/Q)Q]Forskindoserates(mrem/sec):

DR,~p(mrem/sec)=

3.17E-SE,[(L,(X/Q),

+1.11(SF)(B(+g(X/Q)~))Q+...(L;+1.11(SF)M;)

(X/Q)Q.)

Where:DRDR+pV)totalbodygammadoserate(mrem/sec).

skindoseratefromgammaandbetaradiation (mrem/sec).

theconstantaccounting forthegammawholebodydoseratefromstackradiation foranelevatedfiniteplumereleasesforeachidentified noblegasnuclide,i.ListedonTable3-2inmrem/yrperpCi/sec.theconstantaccounting forthegammawholebodydoseratefromimmersion inthesemi-infinite cloudforeachidentified noblegasnuclide,i.ListedinTable3-3inmrem/yrperpCi/m(fromReg.Guide1.109)QiQ.thereleaserateofisotopeifromthestack(s)orvent(v);(pCi/sec)

SFX/Qstructural shielding factor.therelativeplumeconcentration (inunitsofsec/m')atthelandsectorsiteboundaryorbeyond.Averagemeteorological data(Table3-1)isused."Elevated" X/Qvaluesareusedforstackreleases(s=stack);"Ground"X/QvaluesareusedforEmergency Condenser Ventreleases(v=vent).Litheconstantaccounting forthebetaskindoseratefromimmersion inthesemi-infinite cloudforeachidentified noblegasnuclide,i.ListedinTable3-3inmrem/yrperpCi/m~(fromReg.Guide1.109)B;theconstantaccounting fortheairgammaradiation fromtheelevatedFiniteplumeresulting fromstackreleasesforeachidentified noblegasnuclide,i.ListedinTable3-2inmrad/yrperpCi/sec.004152LL-17-Unit1ODCMRevision14June1994

3.2.1.1NobleOases(Cont'd)theconstantaccounting forthegammaairdoseratefromimmersion inthesemi-infinite cloudforeachidentified noblegasnuclide,i.ListedinTable3-3inmrem/yrperpCi/m~(fromReg.Guide1.109)3~2~1.2SeeAppendixBforderivation ofB,andV,.Tritium,ZodinesandParticulates Toensurethatthe1500mrem/year sitedoseratelimitisnotexceeded, offsitedoseratesfortritium,iodineandparticulates withhalflivesgreaterthan8daysshallbecalculated monthlyandwhenreleaserates(Q)exceed0.34pCi/secusingthefollowing equation.

D~(mrem/sec)

=3.17E-BEj[E, R~[W,Q+WQ.])Where:WjTotaldoseratetoeachorgankofanindividual inagegroupa(mrem/sec).

dispersion parameter eitherX/Q(sec/m~)orD/Q(1/m~)depending onpathwayandreceptorlocationassumed.Averagemeteorological dataisused(Table3-1)."Elevated" Wjvaluesareusedforstackreleases(s=stack);"Ground"WjvaluesareusedforEmergency Condenser Ventreleases(v=vent).thereleaserateofisotopei,fromthestack(s)orvent(v);(pCi/sec).

thedosefactorforeachisotopei,pathway),agegroupa,andorgank(Table3-4,through3-22;m'-mrem/yr perpCi/secforallpathwaysexceptinhalation, mrem/yrperpCi/m~.TheRvaluescontained inTables3-4through3-22werecalculated usingthemethodology definedinNUREG-0133 andparameters fromRegulatory Guide1.109,Revisionliaspresented inAppendixC.3.17E-8=theinverseofthenumberofsecondsinayear.Whenthereleaserateexceeds0.34pCi/sec,thedoserateassessment shallalsoincludeJAFandNMP-2contribution.

Theuseofthe0.34pCi/secreleaseratethreshold toperformdoseratecalculations is)ustified asfollows:(a)The1500mrem/yrorgandoseratelimitcorresponds toaminimumreleaseratelimitof0.34pCi/seccalculated usingtheequation:

1500~(Q,pCi/sec)x(+Wj)Where:1500(RgWj)siteboundarydoseratelimit(mrem/year).

themaximumcurie-to-dose conversion factorequalto4.45E3mrem-sec/pCi-yr forSr-90,childboneatthecriticalresidence receptorlocationbeyondthesiteboundary.

004152LL-18-Unit1ODCMRevision14June1994

3.2.1.2Tritium,IodinesandParticulates'(Cont'd)

(b)Theuseof0.34pCi/secreleaseratethreshold andthe4.45E3mrem-sec/pCi-yr curie-to-dose conversion factorisconservative sincecurie-to-dose conversion factorsforotherisotopeslikelytobepresentaresignificantly lower.Inaddition, iftheorgandoserateexceeds5%oftheannuallimit,thefollowing procedural actionswillbetaken:1)NotifytheUnit1SSS(StationShiftSupervisor) andUnit1Supervisor Chemistry.

2)3)NotifytheUnit2SSSandUnit2Supervisor Chemistry andrequesttheUnit2contribution tooffsitedose.NotifytheSSSoftheJamesA.Fitzpatrick contribution tooffsitedose.4)Increasethefrequency ofperforming dosecalculations ifnecessary toensuresite(NineMilePointUnits1and2andFitzpatrick) limitsarenotexceeded.

3~2~2DoseCalculations willbeperformed monthlyataminimum,todemonstrate thatdosesresulting fromthereleaseofnoblegases,tritium,iodines,andparticulates withhalflivesgreaterthan8daysarewithinthelimitsspecified in10CFR50,AppendixI.Theselimitsare:NobleGases5mRgamma/calendar quarter10mradbeta/calendar quarter10mRgamma/calendar year20mradbeta/calendar yearTritiumIodinesandParticulates 7.5mremtoany-organ/calendar quarter15mremto,anyorgan/calendar year3.2.2.1NobleGasAirDoseThefollowing NobleGasairdoseequationincludescontributions fromthestack(s)elevatedreleaseandtheemergency condenser vent(v)groundlevelreleasewhenapplicable (seesection3.2):Forgammaradiation'mrad):

D(mrad)3.17E-BE,(M,(X/Q)

Q+(B;+g(X/Q),)Q.)~tForbetaradiation (mrad):D>(mrad)~3.17E-SE~N,[(X/Q)Q+

(X/Q),Q)~tWhere:gammaairdose(mrad).betaairdose(mrad).NotethattheunitsforthegammaairdoseareinmradcomparedtotheunitsforthelimitsareinmR.TheNRCrecognizes that1mR=1mrad,forgammaradiation.

004152LL-19-Unit1ODCMRevision14June1994

3.2~2~1B(N,NobleGasAirDose(Cont'd)'Itheconstantaccounting fortheairgammaradiation fromtheelevatedfiniteplumeresulting fromstackreleasesforeachidentified noblegasnuclide,i.ListedinTable3-2inmrad/yrperpCi/sec.Theconstantaccounting fortheairbetadosefromimmersion inthesemi-infinite cloudforeachidentified noblegasnuclide,i.ListedonTable3-3inmrad/yrperpCi/m(fromReg.Guide1.109).Q.,Q.=thereleaserateofisotopei,fromthestack(s)orvent(v);(pCi/sec)

.3.17E-8=theinverseofthenumberofsecondsinayear..theconstantaccounting fortheairgammadosefromimmersion inthesemi-infinite cloudforeachidentified noblepasnuclide,i.ListedonTable3-3inmrad/yrperpCi/m(fromReg.Guide1.109).totaltimeduringreleaseperiod,sec.Allotherparameters areasdefinedinsection3.2.1.1.3.2.2.2Tritium,ZodinesandParticulates Toensurethatthe15mrem/yrfacilitydoselimitisnotexceeded, offsitedosesfortritium,iodines,andparticulates withhalflivesgreaterthan8daysshallbecalculated monthlyusingthefollowing equation:

D~(mrem)317ESZj[E,~[W,Q+WQ))~tWhere:WjQiQtotaldosetoeachorgankofanindividual inagegroupa(mrem).dispersion parameter eitherX/Q(sec/m~)orD/Q(1/m~)depending onpathwayandreceptorlocationassumed.Averagemeteorological dataisused(Table3-1)."Elevated" Wjvaluesareusedforstackreleases(s~stack);"Ground"WjvaluesareusedforEmergency Condenser Ventreleases(v~vent).thereleaserateofisotopeifromstack(s)orvent(v);(pCi/sec)

.3.17E-Sthedosefactorforeachisotopei,pathwayj,agegroupa,andorgank(Tables3-4,through3-22;m~-mrem/yr perpCi/sec).

Rvaluescontained inTables3-4through3-22werecalculated usingthemethodology definedinNUREG-0133 andparameters fromRegulatory Guide1.109,Revision1;aspresented inAppendixC.theinverseofthenumberofsecondsinayear.totaltimeduringthereleaseperiod,sec.004152LL-20-Unit1ODCMRevision14June1994

3.3Accumulating DosesDoseswillbecalculated monthly,ataminimum,forgammaair,betaair,andthecriticalorganforeachagegroup.Doseestimates will,also,becalculated monthlypriortoreceiptofanyoffsiteanalysisdatai.e.,strontium, tritium,andiron-55.Resultswillbesummedforeachcalendarquarterandyear.Thecriticaldosesarebasedonthefollowing:

noblegasplumeairdosedirectradiation from,groundplanedeposition inhalation dosecowmilkingestion dosegoatmilkingestion dosecowmeatingestion dosevegetation (foodcrops)ingestion doseThequarterly andannualresultsshallbecomparedtothelimitslistedinparagraph 3.2.2.Ifthelimitsareexceeded, specialreports,asrequiredbySection6.9.3oftheTechnical Specification, shallbesubmitted.

3'CriticalReceptors, Inaccordance withtheprovisions of10CFR20and10CFR50/AppendixI,thecriticalreceptors havebeenidentified andarecontained inTable3-1.Forelevatednoblegasreleasesthecriticalreceptoristhesiteboundary.

When1985averageannualX/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 pathwayswillbebasedonthegreatestD/Qlocation.

Thislocationhasbeendetermined inconjunction withthelandusecensus(technical specification 3.6.22)andissub)ecttochange.Thevegetation (foodcrop)pathwayisbasedonthegreatestD/Qgardenlocationfromwhichsamplesaretaken.Thislocationmayalsobemodifiedasaresultofvegetation samplingsurveys.Theinhalation andgroundplanedosepathwayswillbecalculated atthecriticalresidence.

BecausetheTechnical Specifications statetocalculate "atthesiteboundaryandbeyond",thedosesand/ordoseratesmustbecalculated foramaximumindividual whoisexposedtoallpathwaysat.thesiteboundaryandatthecriticalresidence.

Themaximumindividual isacomposite ofthehighestdosefactorofeachagegroup,foreachor'ganandtotalbody,andeachnuclide.Sincethecrit,icalresidence locationhasthegreatestoccupancy time,theresultant doseattheresidence including allpathwaysislimiting.

However,duetotheTechnical Specification wording,theinhalation andgroundplanedoseatthesiteboundaryalongwithallotherpathways, willbecalculated assumingacontinuous occupancy time.004152LL-21-Unit1ODCMRevision14June1994

3~3CriticalReceptors (Cont'd)3.4Znlieuofcorrecting landsiteboundarygroundplaneandinhalation dosefactorsforoccupancy time,aTechnical Specification changewillbesubmitted tochangetherequirement fromcalculating "atthesiteboundaryandbeyond"to"atthesiteboundaryorbeyond".Unit1willthencalculate atthe,criticalresidence sincethisshouldbethelimitingdose.Untilthischangeiseffective, thedoseand/ordoseratecalculations fortritium,iodines,andparticulates withhalflivesgreaterthan8dayswillconservatively assumethatthegroundplaneandinhalation pathwaycriticalreceptors areatthesiteboundary, i.e.,X/QandD/Q,respectively, arecalculated atthesiteboundary.

Refinement ofOffsiteDosesResulting fromEmergency Condenser VentReleasesThedosesresulting fromtheoperation oftheemergency condensers andcalculated inaccordance with3.2.2mayberefinedusingdatafromactualenvironmental samples.Grounddeposition sampleswillbeobtainedfromanareaorareasofmaximumprojected deposition.

Theseareasareanticipated tobeatornearthesiteboundaryandnearprojected plumecenterline.

Usingthemethodology foundinRegulatory Guide1;109,thedosewillbecalculated tothemaximumexposedindividual.

Thisdosewillthenbecomparedtothedosecalculated inaccordance with3.2.2.Thecomparison willresultinanadjustment factoroflessthanorgreaterthanonewhichwillbeusedtoadjusttheotherdosesfromotherpathways.

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

etc.Theadjustment factorsfromthesepathwaysmaybeappliedtothedosescalculated per3.2.2onapathwaybypathwaybasisorseveralpathwayadjustment factorsmaybeaveragedandusedtoadjustcalculated doses.Dosescalculated fromactualenvironmental samplemediawill.bebasedonthemethodology presented inRegulatory Guide1.109.Theregulatory guideequations maybeslightlymodifiedtoaccountforshortintervals oftime(lessthanoneyear)ormodifiedforsimplicity purposesbydeletingdecayfactors.Deletionofdecayfactorswouldyieldmoreconservative results.004152LL-22-Unit1ODCMRevision14June1994

a.o40CFR190REQUIREMENTS

'IThe"UraniumFuelCycle"isdefinedin40CFRPart190.02(b)asfollows:"Uraniumfuelcyclemeanstheoperations ofmillingofuraniumoreichemicalconversion ofuranium,isotopicenrichment ofuranium,fabrication ofuraniumfuel,generation ofelectricity byalight-water-cooled nuclearpowerplantusinguraniumfuel,andreprocessing ofspenturaniumfuel,totheextentthatthesedirectlysupporttheproduction ofelectrical powerforpublicuseutilizing nuclearenergy,butexcludesminingoperations, operations atwastedisposalsites,transportation ofanyradioactive materialinsupportoftheseoperations, andthereuseofrecovered non<<uranium specialnuclearandby-product materials fromthecycle."Section3.6.15.doftheTechnical Specifications requiresthatwhenthecalculated dosesassociated withtheeffluentreleasesexceedtwicetheapplicable quarterorannuallimits,thelicenseeshallevaluatethecalendaryeardosesand,ifrequired, submitaSpecialReporttotheNRCandlimitsubsequent releasessuchthatthedosecommitment toarealindividual fromalluraniumfuelcyclesources.islimitedto25mremtothetotalbodyoranyorgan(exceptthethyroid,whichislimitedto75mrem).Thisreportistodemonstrate thatradiation exposures toallrealindividuals fromalluraniumfuelcyclesources(including allliquidandgaseouseffluentpathwaysanddirectradiation) arelessthanthelimitsin40CFRPart190.Ifreleasesthatresultindosesexceeding the40CFR190limitshaveoccurred, thenavariancefromtheNRCtopermitsuchreleaseswillberequested andifpossible, actionwillbetakentoreducesubsequent releases.

ThereporttotheNRCshallcontain:1)Identification ofalluraniumfuelcyclefacilities oroperations within5milesofthenuclearpowerreactorunitsatthesitethatcontribute totheannualdoseofthemaximumexposedmemberofthepublic.2)Identification ofthemaximumexposedmemberofthepublicandadetermination ofthetotalannualdosetothispersonfromexistingpathwaysandsourcesofradioactive effluents anddirectradiation.

Thetotalbodyandorgandosesresulting fromradioactive materialinliquideffluents fromNineMilePointUnit1willbesummedwiththemaximumdosesresulting fromthereleasesofnoblegases,radioiodines, andparticulates fortheothercalendarquarters(asapplicable) andfromthecalendarquarterinwhichtwicethelimitwasexceeded.

Thedirectdosecomponents willbedetermined byeithercalculation oractualmeasurement.

Actualmeasurements willutilizeenvironmental TLDdosimetry.

Calculated measurements willutilizeengineering calculations todetermine apro)ected directdosecomponent.

Intheeventcalculations areused,themethodology willbedetailedasrequiredinSection6.9.1.eoftheTechnical Specifications.

004152LL-23-Unit1ODCMRevision14June1994

40CFR190REQUIREMENTS (Cont'd)ThedosesfromNineMilePointUnit1willbeaddedtothedosestothemaximumexposedindividual thatarecontributed fromotheruraniumfuelcycleoperations within5milesofthesite.Otheruraniumfuelcyclefacilities within5milesoftheSiteincludeNineMilePointNuclearStationUnit2andtheJamesA.Fitzpatrick NuclearPowerPlant.Dosesfromotherfacilities willbecalculated inaccordance witheachfacilities'DOM.

Forthepurposeofcalculating doses,theresultsoftheRadiological Environmental Monitoring Programmaybeincludedforproviding morerefinedestimates ofdosestoarealmaximumexposedindividual.

Estimated doses,ascalculated fromstationeffluents, maybereplacedbydosescalculated fromactualenvironmental sampleresults.Reportswillincludeallsignificant detailsofthedosedetermination ifradiological samplingandanalysesareusedtodetermine ifthedoselimitsof40CFR190areexceeded.

F1Evaluation ofDosesFromLiquidEffluents Fortheevaluation, ofdosestorealmembersofthepublicfromliquideffluents, thefishconsumption andshoreline sedimentgrounddosewillbeconsidered.

Sincethedosesfromotheraquaticpathwaysareinsignificant, fishconsumption andshoreline sedimentaretheonlytwopathwaysthatwillbeconsidered.

Thedoseassociated withfishconsumption maybecalculated usingeffluentdataandRegulatory Guide1.109methodology orbycalculating adosetomanbasedonactualfishsampleanalysisdata.Becauseofthenatureofthereceptorlocationandtheextensive fishinginthearea,thecriticalindividual maybeateenageroranadult.Thedoseassociated withshoreline sedimentisbasedontheassumption thattheshoreline wouldbeutilizedasarecreational area.ThisdosemaybederivedfromliquideffluentdataandRegulatory Guide1.109methodology orfromactualshoreline sedimentsampleanalysisdata.Equations usedtoevaluatedosesfromactualfishandshoreline sedimentsamplesarebasedonRegulatory Guide1.109methodology.

Becauseofthesamplemediumtypeandthehalf-lives oftheradionuclides historically

observed, thedecaycorrected portionsoftheequations aredeleted.Thisdoesnotreducetheconservatism ofthecalculated dosesbutincreases thesimplicity fromanevaluation pointofview.Table3-23presentstheparameters usedforcalculating dosesfromliquideffluents.

Thedosefromfishsamplemediaiscalculated as:Where:Z([Cg(U)(D~)f)(1E+3)~Thetotalannualdosetoorganj,ofanindividual ofagegroupa,fromnuclidei,viafishpathwaypfinmremperyear.lE+3Theconcentration

'ofradionuclide iinfishsamplesinpCi/gram.

=Theconsumption rateoffishinkg/yr.=Gramsperkilogram.

004152LL-24-Unit1ODCMRevision14June1994

4.1Evaluation ofDosesFromLiquidEffluents (Cont'd)(D~)=Theingestion dosefactorforagegroupa,nuclidei,fishpathwayp,andorganj,(Reg.Guide1.109,TableE-11)(mrem/pCi).

~Thefractional portionoftheyearoverwhichthedoseisapplicable.

Thedosefromshoreline.

sedimentsamplemediaiscalculated as:Zi[Cg(U)(4E+4)(0.3)(D~)f)where:=Thetotalannualdosetoorganj,ofanindividual ofagegroupa,fromnuclidei,viathesedimentpathwayp,inmremperyear.~Theconcentration ofradionuclide iinshoreline sedimentinpCi/gram.

U~Theusagefactor,(hr/yr)(Reg.Guide1.109).4E+4~Theproductoftheassumeddensityofshoreline sediment(40kilogrampersquaremetertoadepthof2.5cm)timesthenumberofgramsperkilogram.

0.3=Theshorewidthfactorforalake.D~~~Thedosefactorforagegroupa,nuclidei,sedimentpathways,andorganj.(Rep.Guide1.109,TableE-6)(mrem/hrperpci/m).4.2~Thefractional portionoftheyearoverwhichthedoseisapplicable.

Evaluation ofDosesFromGaseousEffluents Fortheevaluation ofdosestorealmembersofthepublicfromgaseouseffluents, thepathwayscontained insection3.2.2.3oftheODCMwillbeconsidered.

Theseincludethedeposition, inhalation cowsmilk,goatsmilk,meat,andfoodproducts(vegetation).

However,anyupdatedfielddatamaybeutilizedthatconcernslocations ofrealindividuals, realtimemeteorological data,locationofcriticalreceptors, etc.Datafromthemostrecentcensus'andsamplelocationsurveysshouldbeutilized.

Dosesmayalsobecalculated fromactualenvironmental samplemedia,asavailable.

Environmental samplemediadatasuchasTLD,airsample,milksampleandvegetable (foodcrop)sampledatamaybeutilizedinlieuofeffluentcalculational data.Dosestomemberofthepublicfromthepathwayscontained inODCMsection3.2.2.3asaresultofgaseouseffluents willbecalculated usingthedosefactorsofRegulatory Guide1.109orthemethodology oftheODCM,asapplicable.

Dosescalculated fromenvironmental samplemediawillbebasedonthemethodologies foundinRegulatory Guide1.109.004152LL-25-Unit1ODCMRevision14June1994

Evaluation ofDosesFromDirectRadiation Thedosecontribution asaresultofdirectradiation shallbeconsidered whenevaluating whetherthedoselimitations of40CFR190havebeenexceeded.4.4Directradiation dosesasaresultofthereactor;turbineandradwastebuildings andoutsideradioactive storagetanks(asapplicable) maybeevaluated byengineering calculations orbyevaluating environmental TLDresultsatcriticalreceptorlocations, siteboundaryorotherspecialinterestlocations

.Fortheevaluation ofdirectradiation dosesutilizing environmental TLDs,'hecriticalreceptorinquestion, suchasthecriticalresidence, etc.,willbecomparedtothecontrollocations

.Thecomparison involvesthedifference inenvironmental TLDresultsbetweenthereceptorlocationandtheaveragecontrollocationresult.DosestoMembersofthePublicWithintheSiteBoundaryTheSemi-Annual Radioactive EffluentReleaseReportshallincludeanassessment oftheradiation dosesfromradioactive liquidandgaseouseffluents tomembersofthepublicduetotheiractivities insidethesiteboundaryasdefinedbyFigure5.1-1ofthespecifications.

Amemberofthepublic,asdefinedbytheTechnical Specifications, wouldberepresented byanindividual whovisitsthesites'nergy Centerforthepurposeofobserving theeducational displaysorforpicnicking andassociated activities.

Fishingisamajorrecreational activityintheareaandontheSiteasaresultofthesalmonoid andtroutpopulations inLakeOntario.Fishermen havebeenobservedfishingattheshoreline neartheEnergyCenterfromAprilthroughDecemberinallweatherconditions.

Thus,fishingisthemajoractivityperformed bymembersofthepublicwithinthesiteboundary.

Basedonthenatureofthefishermen andundocumented observations, itisconservatively assumedthatthemaximumexposedindividual spendsanaverageof8hoursperweekfishingfromtheshoreline atalocationbetweentheEnergyCenterandtheUnit1facility.

Thisestimateisconsidered conservative butnotnecessarily excessive andaccountsforoccasions whereindividuals mayfishmoreonweekendsoronafewdaysinMarchoftheyear.Thepathwaysconsidered fortheevaluation includetheinhalation pathway,thegrounddosepathwaywiththeresultant wholebodyandskindoseandthedirectradiation dosepathwaywiththeassociated wholebodydose.Thedirectradiation dosepathway,inactuality, includesseveralpathways.

Theseinclude:thedirectradiation gammadosetoanindividual fromanoverheadplume,agammasubmersion plumedose(asapplicable),

possibledirectradiation dosefromthefacilityandagroundplanedose(deposition).

Becausethelocationisincloseproximity tothesite,anybetaplumesubmersion doseisfelttobeinsignificant.

Otherpathways, suchastheingestion pathway,arenotapplicable sincethesedosesareincludedundercalculations fordosestomembersofthepublicoutsideofthesiteboundary.

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

004152LL-26-Unit1ODCMRevision14June1994

.~

DosestoMembersofthePublicWithintheSiteBoundary(Cont'd)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.Table3-23presentsthereference fortheparameters usedinthefollowing equation.

NOTE4Dj,Where:Thefollowing equationisadaptedfromequations C-3andC<<4ofRegulatory Guide1.109.SincemanyofthefactorsareinunitsofpCi/m~,m~/sec.,etc.,andsincetheradionuclide decayexpressions havebeendeletedbecauseoftheshortdistancetothereceptorlocation, theequationpresented hereisnotidentical totheRegulatory Guideequations.

Zl[(CI)F(X/Q)(DFA)i~(BR)at]C,Themaximumdosefromallnuclidestotheorgan)andagegroup(a)inmrem/yr.Theaverageconcentration inthestackreleaseofnuclideifortheperiodinpCi/m~.Unit1averagestackflowrateinm~/sec.X/QTheplumedispersion parameter foralocationapproximately 0.50mileswestofNMP-1gtheplumedispersion parameter is8.9E-06(stack)andwasobtainedfromtheC.T.MainfiveyearaverageannualX/Qtables.Thestack(elevated)

X/Qisconservative whenbasedon0.50milesbecauseofthecloseproximity ofthestackandthereceptorlocation.

(DFA)0,(BR)~Thedosefactorfornuclidei,organ),andagegroupain'mremperpCi(Reg.Guide1.109,TableE-7).Annualairintakeforindividuals inagegroupainm~peryear(obtained fromTableE-5ofRegulatory Guide1.109).Fractional portionoftheyearforwhichradionuclide iwasdetectedandforwhichadoseistobecalculated

('nyears).004152LL-27-Unit1ODCMRevision14June1994

~.4DosestoMembersofthePublicWithintheSiteBoundary(Cont'd)~Thegrounddosepathway(deposition) willbeevaluated byobtaining atleastonesoilorshoreline sedimentsampleintheareawherefishingoccurs.Thedosewillthenbecalculated usingthesampleresults,thetimeperiodinquestion, andthemethodology basedonRegulatory Guide1.109aspresented inSection4.1.Theresultant dosemaybead)ustedforabackground dosebysubtracting theapplicable off-sitecontrolsoilorshoreline sedimentsampleradionuclide activities.

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

Thedirectradiation gammadosepathwayincludesanygammadosesfromanoverheadplume,potential submersion intheplume,possibledirectradiation fromthefacilityandgroundplanedose(deposition).

Thisgeneralpathwaywillbeevaluated byaverageenvironmental TLDreadings.

Atleasttwoenvironmental TLDswillbeutilizedatonelocationintheapproximate areawherefishingoccurs.TheTLDswillbeplacedinthefieldonapproximately thebeginning ofacalendarquarterandremovedonapproximately theendofthecalendarquarter.Forthepurposesof.thisevaluation, TLDdatafromquarters2,3,and4willbeutilized.

TheaverageTLDreadingswillbeadjustedbytheaveragecontrolTLDreadings.

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

IntheeventoflossortheftoftheTLDs,resultsfromaTLDorTLDsinanearbyareamaybeutilized.

004152LL-28-Unit1ODCMRevision14June1994

5~0ENVIRONMENTAL MONITORING PROGRAM5.1SamplingStationsThecurrentsamplinglocations arespecified inTable5-1andFigures5.1-1,5.1-2.Themeteorological towerisshowninFigure5.1-1.ThelocationisshownasTLDlocation17.TheRadiological Environmental Monitoring ProgramisajointeffortbetweentheNiagaraMohawkPowerCorporation andtheNewYorkPowerAuthority, theownersandoperators oftheNineMilePointUnit1andtheJamesA.FitzPatrick NuclearPowerPlant,respectively.

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

Theaveragedispersion anddeposition parameters havebeencalculated fora5yearperiod,1978through1982.Thesedispersion calculations areattachedasAppendixE.Thecalculated dispersion ordeposition parameters willbecomparedtotheresultsoftheannuallandusecensus.Ifitisdetermined thatamilksamplinglocationexistsatalocationthatyieldsasignificantly higher(e.g.50%)calculated D/Qrate,thenewmilksamplinglocationwillbeaddedtothemonitoring programwithin30days'fanewlocationisadded,theoldlocationthatyieldsthelowestcalculated D/QmaybedroppedfromtheprogramafterOctober31ofthatyear.Interlaboratory Comparison ProgramAnalysesshallbeperformed onsamplescontaining knownquantities ofradioactive materials thataresuppliedaspartofaCommission approvedorsponsored Interlaboratory Comparison Program,suchastheEPACrosscheck Program.Participation shallbeonlyforthosemedia,e.g.,air,milk,water,etc.,thatareincludedintheNineMilePointEnvironmental Monitoring Programandforwhichcrosscheck samplesareavailable.

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

-grossbetainairparticulate filters-gammaemittersinairparticulate filters-gammaemittersinmilk-gammaemittersinwater-tritiuminwater-I-131inwater004152LL-29-Unit1ODCMRevision14June1994

Capabilities forThermoluninescent Dosimeters UsedforEnvironmental Measurements 5~3.1Requireddetection capabilities forthermoluminescent dosimeters usedforenvironmental measurements requiredbyTable4.6.20-1, footnoteboftheTechnical Specifications arebasedonANSIStandardN545,section4.3.TLDsaredefinedasphosphors packagedforfielduse.Inregardtothedetection capabilities forthermoluminescent dosimeters, onlyonedetermination isrequiredtoevaluatetheabovecapabilities pertypeofTLD.Furthermore, theabovecapabilities maybedetermined bythevendorwhosuppliestheTLDs.Requireddetection capabilities areasfollows:Uniformity shallbedetermined bygivingTLDsfromthesamebatchanexposureequaltothatresulting fromanexposurerateof10mR/hrduringthefieldcycle.Theresponses obtainedshallhavearelativestandarddeviation oflessthan7.5%.Atotalofatleast5TLDsshallbeevaluated.

5.3.2Reproducibility shallbedetermined bygivingTLDsrepeatedexposures equaltothatresulting fromanexposurerateof10uR/hrduringthefieldcycle.Theaverageoftherelativestandarddeviations oftheresponses shallbelessthan3.0%.Atotalofatleast4TLDsshallbeevaluated.

5,33Dependence ofexposureinterpretation onthelengthofafieldcycleshallbeexaminedbyplacingTLDsforaperiodequaltoatleastafieldcycleandaperiodequaltohalfthesamefieldcycleinanareawhere.theexposurerateisknowntobeconstant.

Thistestshallbeconducted underapproximate averagewintertemperatures andapproximate averagesummertemperatures.

Forthesetests,theratiooftheresponseobtainedinthefieldcycletotwicethatobtainedforhalfthefieldcycleshallnotbelessthan0.85.Atleast6TLDsshallbeevaluated.

5'.4Energydependence shallbeevaluated bytheresponseofTLDstophotonsforseveralenergiesbetweenapproximately 30keVand3MeV.Theresponseshallnotdifferfromthatobtainedwiththecalibration sourcebymorethan25%forphotonswithenergiesgreaterthan80keVandshallnotbeenhancedbymorethanafactoroftwoforphotonswithenergieslessthan80keV.Atotalofatleast8TLDsshallbeevaluated.

5~3.5Thedirectional dependence oftheTLDresponseshallbedetermined bycomparing theresponseoftheTLDexposedintheroutineorientation withrespecttothecalibration sourcewiththeresponseobtainedfordifferent orientations.

Toaccomplish this,theTLDshallberotatedthroughatleasttwoperpendicular planes.Theresponseaveragedoveralldirections shallnotdifferfromtheresponseobtainedinthestandardcalibration positionbymorethan10%.Atotalofatleast4TLDsshallbeevaluated.

5.3~6Lightdependence shallbedetermined byplacingTLDsinthefieldforaperiodequaltothefieldcycleunderthefourconditions foundinANSIN545,section4.3.6.Theresultsobtainedfortheunwrapped TLDsshallnotdifferfromthoseobtainedfortheTLDswrappedinaluminumfoilbymorethan10%.Atotalofatleast4TLDsshallbeevaluated foreachofthefourconditions.

004152LL-30-Unit1ODCMRevision14June1994

53~7~~Moisturedependence shallbedetermined byplacingTLDs(thatis,thephosphors packagedforfielduse)foraperiodequaltothefieldcycleinanareawheretheexposurerateisknowntobeconstant.

TheTLDsshallbeexposedundertwoconditions:

(1)packagedinathin,sealedplasticbag,and(2)packagedinathin,sealedplasticbagwithsufficient watertoyieldobservable moisturethroughout thefieldcycle.TheTLDorphosphor, asappropriate, shallbedriedbeforereadout.TheresponseoftheTLDexposedintheplasticbagcontaining watershallnotdifferfromthatexposedintheregularplasticbagbymorethan10%.Atotalofatleast4TLDsshallbeevaluated foreachcondition.

5.3.8Selfirradiation shallbedetermined byplacingTLDsforaperiodequaltothefieldcycleinanareawheretheexposurerateislessthan10uR/hrandtheexposureduringthefieldcycleisknown.Ifnecessary, corrections shallbeappliedforthedependence ofexposureinterpretation onthelengthofthefieldcycle(ANSIN545,section4.3.3).Theaverageexposureinferredfromtheresponses oftheTLDsshallnotdifferfromtheknownexposurebymorethananexposureequaltothatresulting fromanexposurerateof10uR/hrduringthefieldcycle.Atotalofatleast3TLDsshallbeevaluated.

004152LL-31-Unit1ODCMRevision14June1994

TABLE1-1AverageEnergyPerDisintegration ISOTOPEAr-41Kr-83mKr-85Kr-85mKr-87Kr-88Kr-89Kr-90Xe-131MXe-133Xe-133mXe-135Xe-135mXe-137Xe-1381.2940.002480.00220.1590.7931.952'22.100.02010.04540.0420.2470.4320.1941.18~Ref(3)(2)(2)~Eevdie(e0.4640.03710.2500.2531.320.3771.371.010.1430.1350.190.3170.0951.640.611~Ref(3)(2)(2)(2)(3)(4)ORNL-4923, Radioactive Atoms-SulementI,M.S.Martin,November1973.NEDO-12037, "SummaryofGammaandBetaEmittersandIntensity Data";M.E.Meek,R.S.Gilbert,January1970.(TheaverageenergywascomputedfromthemaximumenergyusingtheICRPIIequation, notthe1/3valueassumption usedinthisreference).

NCRPReportNo.58,"AHandbookofRadioactivity Measurements Procedures";

1978Theaverageenergy.includesconversion electrons.

004152LL-32-Unit1ODCMRevision14June1994

TABLE2-1~VALUES-LIQUID*RADWASTETANKINFANTmrem-mlhr-pCiNUCLIDEBONELIVER2.90E-1H3Cr51Cu64Mn541.13E-11.87E+18.444.96E+13.341.02E+15.91E+15.23E-24.232'61.96E+18.342:40E+12.73E+16.66E+14.43E+33.30E-24-15E-54.572.371.91E-14.14FE551.31E+1Fe592.84E+1Co58Co60Zn651.72E+1Sr892.32E+32.87E+1Sr901.74E+4Zr951.91E<<14.66E-25.02E-22.07E-43.50E+12'7Mn56~-Mo992.40E-42.34E+12.373.54E+16.152.37Na242.37I1313.03E+11.57E+11.17E+44.17E+14.22I133Ni65I132Cs134Cs136Cs137Ba140Ce1411.801.12E+37.231.33E-31.51E-41.58E-43.21E-43.54E+26.60E+24.05E+11.19E+24.91E+25.75E+26.85E-51.14E-41.50E-23.58E-46.67E+14.45E+14.07E+11.70E+24.75E+1154E+23.57E-21~36E-21.14E-21.50E+21.50E-17.747'1E-24.40E-25.17E-39.18E-31.20E-31.57E-1Nb953.85E-21.59E-2La1401.18E-24.67E-34.62E-1Ce1442.791.14TBODYTHYROIDKIDNEY2.90E-12.90E-12.90E-11.29E-28.39E-31.83E-3LUNGGI-TRACT2.90E-12.90E-11.63E-23.75E-14.132.326.86l.071.47E+12.37E+12.378.332.42E+15.00E+14.77E+12.17E+2232E+12.18E-27'12371281.041.15E-22.60E-46.97E+11.799.71E+11.816.24E+11.809.23E-23.69E+12.27E+11.34E+15.48E+11.60E+2*Calculated inaccordance withNUREG0133,Section4.3.1;andRegulatory Guide1.109,Regulatory positionC,Sectionl.004152LL-33-Unit1ODCMRevision14June1994

NUCLIDEBONELIVERH34.39E-lCr512.13E-22.13E-2Cu642.51E-62.70Mn546.923.38E+3Fe559.21E+24.88E+2Fe591.30E+32.11E+3Co581.897.46E+11.401.637.86E-12.30E-12.51E-66.529.06E+26.921.51E+21.05E+31.342'4E+21-899.53E+21.341.89TABLE2-224,VALUES-LIQUID*RADWASTETANKCHILDmrem-mlhr-pCiTBODYTHYROIDKIDNEY4.39E-14.39E-14.39E-1LUNGGI-TRACT1.427'1E+12.51E-61.27E+26922.84E+32.76E+29.05E+16.12E+22.19E+3'~894.26E+24.39E-14.39E-1Co601.12E+23.28E+27.48E+21.12E+21.12E+21.12E+21.31E+3Cs136Cs1373.52E+49.67E+45.15E+54.93E+5Ba1403.61E+23.96E-lCe1411.50E-11.07E-lNb95La1405.21E+22.03E+21.50E-15.93E-2Ce1445.001.81Zn652.15E+45.73E+4Sr893.26E+41.10E-4Sr904.26E+5Zr951.701.33Mn561.65E-1Mo995.35E-39.57E+1Na241.52E+21.52E+2I1312.09E+22.10E+2I1333.39E+14.19E+1Ni652.67E-12'1E-2I1326.13E-31.13E-2Cs1343.68E+56.04E+53.56E+43.853~61E+49.32E+21.10E-41.10E-41.08E+51.323.73E-21.231.382.00E-12.37E+15.35E-32.04E+21.52E+21.52E+21.52E+21.19E+26.94E+43.45E+21.59E+17.78E+36.98E+11.47E-25.18E-35.22E-11.72E-2127E+53.54E+11.87E+56.26E+46.21E-15.15E+47.28E+45.37E+11.61E+52.11E+17.96E-21.82E-16.99E-26.34E-28.24E-21.45E+26.39E-11.91E+22.68E-2103E-21.03E-26.06E-13.58E-11.163851.01E+41~10E-41.26E+31~235.74E+31.08E+22.39E+15.35E-37.91E+11.52E+21.52E+25.60E-21~87E+11.38E-41.69E+13.081.32E-26.72E+43.29E+37.68E+33.40E+35.78E+43.14E+32.68E-11.83E+26.34E-25.40E+16.39E-13.75E+51.03E-21.36E+33.58E-13.80E+2*Calculated inaccordance withNUREG0133,Section4.3.1;andRegulatory Guide1.109,Regulatory positionC,Sectionl.004152LL-34-Unit1ODCMRevision14June1994

Mn561.81E-1NUCLIDEBONELIVERH33.28E-1Cr511.02E-11.02E-1Cu641.20E-52.89Mn543.31E+14.34E+3Fe556.94E+24.92E+2Fe591.07E+3'.49E+3Co589.039.82E+1Co605.36E+27.96E+2Zn652.10E+47.28E+4Sr892.44E+45.24E-4Sr904.66E+5Zr956.206.001.15E+29.64E+26.412.15E+2,9.036.419.031.12E+35.36E+25'6E+23'0E+41.84E+14.66E+46.98E+25.24E-45.24E-41.15E+55.975.903.22E-26.042.29E-1TABLE2-3A,VALUES-LIQUID*RADWASTETANKTEENmrem-mlhr-pCiTBODYTHYROIDKIDNEY3.28E-13.28E-13.28E-11.398.16E-1384E-11.361.20E-57.32887E+2'.31E+11.32E+3ILUNGGI-TRACT1.942'6E+21.20E-S2'4E+23.31E+18.86E+33.12E+22'3E+27.89E+25.87E+39.031.24E+35.36E+23.93B+31.84E+13.08E+45.24E-42.90E+35.901.31E+42.28E+21.19E+13.28E-13.28E-12.56E-21.65E+21.39E+21.39E+22.68E-14.30E+16.60E-43.25E+1Mo992.56E-29.22E+1Na241.39E+21.39Ei2I1311.55E+22.17E+21.76E+12.56E-22.11E+21.39E+21.39E+21.39E+21.16E+26.31E+43.73E+21.31E+15.99E+37.52E+14.29E+12.66E-21.28E-2I1332.53E+1Ni652.08E-11.441.21E-25.59E-34.60E-34.32E-12.02E-2I1324.90E-2Cs1343.05E+58.73E+49.10E+31.01E+49.44E+37.18E+53.33E+51.69E+22.28E+57.88E+42.97Cs1362.98E+41.17E+5Cs1374.09E+55.44E+5Ba1402.35E+24.10E-1Ce1413.46E-13.32E-16.38E+41.55E+13~81E-14.79E-13.07E-13.04E-13.17E-15.75E-13.63E+23.04E-18.16E+11.90E+52.57E+21.85E+5'.21E+47.99E+3Nb95La140Ce1443.992.654.44E+22.48E+21.57E-11.02E-11.18E+23.062.40E+21.831.712276.35E-24.94E-24.94E-23.061.05E+64.94E-23.05E+35.74E+21.71*Calculated inaccordance withNUREG0133,Section4.3.1;andRegulatory Guide1.109,Regulatory positionC,Sectionl.004152LL-35-Unit1ODCMRevision14June1994

NUCLIDEBONEH3Cr511.82E-2Cu64Mn545.94Fe556.64E+2Fe591.03E+3Co58-l.62LIVER4.45E-11-82E-22.754.38E+34.58E+22.43E+39.15E+11277.64E-12.93E-11.298.41E+25.946.941.31E+31.07E+29.31E+22.03E+21.151.621~15l.62TABLE2-4A,VALUES-LIQUID*RADWASTETANKADULTmrem-mlhr-pCiTBODYTHYROIDKIDNEY4.45E-14.45E-14.45E-1LUNGGI-TRACT1.675.943.14E+22.35E+21.34E+42.56E+22.63E+26.79E+28.09E+31.621.82E+34.45E-14.45E-1Co609.60E+12.57E+26.71E+29.60E+19.60E+1960E+14.99E+3Zn652.31E47.36E+43.32E+43.304.92E+43.304.63E+4Sr892.25E+49.39E-56'5E+29.39E-59.39E-59.39E-S3.60E+3Sr905.60E+5Zr951.36Mn561-15E1.73E-11.37E+51.123.07E-21.06l.21220E-11.061.62E+43.06E+25.52Mo994.58E-38.70E+1Na241.35E+21.35E+2I1311.45E+22.07E+2I133235E+14.09E+11.66E+14.58E-31.97E+21.35E+21.35E+21.35E+21.19E+26.79E+43.55E+21.25E+16.02E+37.14E+14-58E-32.02E+21.35E+21.35E+2480E-25.47E+1118E-43.68E+1Ni65I132Cs134Cs136Cs1371.93E-12.51E-24.68E-31.25E-22.98E+57.08E+52.96E+43'2E+51.17E+55.22E+51.14E-24.38E-34.38E-12.00E-25.79E+53.03E+12.29E+58.42E+45.32E-16.51E+43.42E+54.60E+11.77E+5Ce1419.53E-28.20E-2Nb954.39E+22.44E+2La1401.11E-16.03E-2Ce1442.481.225.75E-25.44E-26.72E-21.32E+25.47E-12.41E+22.24E-28.84E-38.84E-34.24E-13.07E-18.47E-1Ba1402.24E+23.49E-1,1.47E+16.83E-21.64E-16.36E-12.35E-37.61E+41.24E+48.93E+31.33E+4590E+41.02E+42.29E-l4.61E+25.44E-21.06E+25.47E-11.48E+68.84E-33.78E+33.07E-17.37E+2*Calculated inaccordance withNUREG0133,Section4.3.1yandRegulatory Guide1.109,Regulatory positionC,Section1.004152LL-36-Unit1ODCMRevision14June1994

NUCLIDEBONELIVERH37.43E-4TABLE2-5A,VALUES-LIQUID*EMERGENCY CONDENSER VENTINFANTmrem-mlhr-pCiTBODYTHYROIDKIDNEY743E-47.43E-47.43E-4LUNGGI-TRACT7.43E-47.43E-4Cr513.30E-S2.15E-54.70E-64.18E-S9'1E-4Cu642.89E-41.34E-44.89E-41.06E-2Fe597.29E-21.27E-1Co588.58E-3Co602.60E-2Zn654.42E-21.52E-1Sr895.95Sr904.46E+1Zr954.90E-41.19E-4Mn566.17E-7Mo996.00E-2Na246.07E-36.07E-3I1317.77E-29.16E-2I1331.08E-21.58E-25.02E-22'4E-26.15E-26.99E-21.71E-11.14E+18.47E-S1.06E-71.17E-27.35E-21.29E-4530E-78.97E-26.07E-36.07E-36.07E-34.03E-23.01E+11.07E-14.62E-32.871.85E-2Mn544.79E-21.08E-2Fe553.35E-22.16E-25.78E-35.94E-31.76E-21~06E-22.75E-33.76E-26.08E-22.14E-,26.19E-21~28E-11.22E-15.57E-15.95E-25.60E-51.98E-26.07E-36.07E-33'7E-32.67E-3Cs136Cs137Ba140Ce141Nb95La140Ce1441.04E-13.06E-11.261.473.85E-13.85E-41~85E-41.13E-49.88E-54.07E-S3.03E-51.20E-S7'6E-32.93E-3Ni653.41E-63.86E-7I1324.05E-78.22E-7Cs1349.08E-l1.691.76E-72.93E-71.71E-11.14E-11.04E-11.99E-21.33E-S2.35E-53.08E-64.02E-43.85E-5917E-74.36E-11.22E-13.95E-19.15E-53.48E-52.92E-S1.19E-3294E-5666E-71.79E-14.60E-32,49E-2464E-31.60E-14.61E-32.37E-49.47E-25'2E-23.43E-21.41E-14.11E-1*Calculated inaccordance withNUREG0133,Section4.3.1;andRegulatory Guide1.109,Regulatory positionC,Sectionl.004152LL-37-Unit1ODCMRevision14June1994 0

NUCLIDEBONELIVERH31.44E-lCr513.78E-S3.78E-SCu642.63Mn541.23E-23.36E+3Fe559.04E+24.79E+2Fe591.28E+32.07E+3Co583.36E-37.01E+1Co601.99E-12.08E+2Zn652.15E+45.73E+4Sr893.07E+4Sr904.01E+5TABLE2-6A,VALUES-LIQUID*EMERGENCY CONDENSER VENTCHILDmrem-mlhr-pCiTBODYTHYROIDKIDNEY144E-11.44E-11.44E-11.371.597.58E-12.07E-16.358.95E+21.23E-29.42E+21.49E+21.03E+32.38E-32.38E-32.15E+23'6E-33.36E-36.14E+21.99E-11.99E-13.56E+46.84E-33.61E+48.78E+21.02E+5Mn561.65E-1Mo998.16E+13.73E-22.02E+12.00E-11.74E+2Na241.50E+21.50E+2I1311.86E+21.87E+2I1333.08E+13.81E+11.50E+21.50E+21.50E+21.06E+26.19E+43.08E+21.44E+17.07E+36.35E+1Zr953.01E-16.78E-2'6.06E-22.19E-39.61E-2LUNGGI-TRACT144E-11.44E-11.387.24E+1123E+21.23E-22.82E+32.71E+28.88E+16.00E+22.15E+33.36E-34.09E+21.99E-11.15E+36.84E-31.01E+41.19E+35.40E+32.19E-36.84E+12'9E+16.75E+11.50E+21.50E+21.67E+11.53E+1Ni652.66E-12.50E-2I1326.01E-31.10E-2Cs1343.68E+56.04E+5Cs136Cs137Ba140Ce1413.51E+49.66E+45.14E+54.92E+52.48E+22.17E-13.08E-21.54E-2Ce1441.645.15E-1Nb955.21E+22.03E+2La1401.31E-14.59E-21.46E-25.OBE-35.12E-11.69E-21.27E+56.29E-21.87E+56.25E+41.10E-35.14E+43.071.30E-26.71E+43.25E+37.67E+33.40E+31.45E+11.42E-47.09E-22.39E-31.13E-46.83E-31.45E+21.14E-31.90E+21.55E-21.83E-S1.83E-58.81E-26.36E-42.85E-11.30E-11.26E+21.13E-41.91E+11.14E-33.75E+51.83E-S1.28E+36.36E-41.34E+2727E+49.55E-2160E+5'.77E+43.08E+3*Calculated inaccordance withNUREG0133,Section4.3.1;andRegulatory Guide1.109,Regulatory positionC,Section1.004152LL-38-Unit1ODCMRevision14June1994

NUCLIDEBONEH3LIVER1.74E-1TABLE2-7~VALUES-LIQUID*EMERGENCY CONDENSER VENTTEENmrem-mlhr-pCiTBODYTHYROIDKIDNEY1.74E-l1.74E-11~74E-1LUNGGI-TRACT1.74E-11.74E-1Cu642.86Cr511.81E-41.81E-41.281.357.12E-12.81E-17'41~832.15E+22.22E+2Mn545.89E-24.29E+3Fe556.89E+2Fe591.05E+34.88E+22.46E+3Zn652.10E+4Sr892.38E+4Sr904.54E+5Zr952.56E-1Mn56Mo997.28E+48.80E-21.81E-18.57E+1Na241.38E+21.38E+2I1311.47E+22.06E+2I1332.42E+14.11E+1Cs136Cs137Ba140Ce141Nb95La1402.08E-12.66E-24.86E-31.27E-23.05E+57.18E+52.98E+41.17E+54.09E+55.44E+51.96E+22'7E-22.43E-21.64E-24.41E+22.45E+21.05E-15.17E-2Ce1441.275.28E-1Co581.61E-28.78E+1Co609.53E-l2.57E+23.22E-21.63E+12.29E-11.96E+21.38E+21.38E+21.38E+21.10E+26.00E+43.54E+21.25E+15.74E+37.21E+11~21E-24.56E-34.29E-12.00E-23.33E+53.01E-12.28E+57.87E+45.28E-36.38E+41.89E+54.57E-l1.85E+51.27E+16.77E-48.23E-22.36E-35.40E-48.02E-31.15E+25.43E-32.37E+21.38E-2878E-5878E-57.12E-23.04E-33.17E-18.52E+25.89E-2128E+31.14E+29.50E+21.14E-21.14E-22.02E+21.61E-21.61E-25.78E+29.53E-19.53E-13.39E+43.28E-24.66E+46.81E+21.12E+56.38E-21.05E-21.24E-15.89E-28.81E+33.10E+22.11E+27.76E25.82E+31.61E-21.21E+39.53E-l3.34E+33.28E-23'8E+42.83E+31.27E+41.05E-21.79E+21.19E+11.54E+21.38E+21.38E+24.77E-44.07E+13.11E+11.445.54E-38.71E+48.93E+31.01E+49.43E+37.19E+47.73E+31.62E-13.03E+25.40E-44.54E+15.43E-31.05E+68.78E-52.96E+33.04E-33.19E+2*Calculated inaccordance withNUREG0133,Section4.3.1;andRegulatory Guide1.109,Regulatory positionC,Sectionl.004152LL-39-Unit1ODCMRevision14June1994

H32.27E-lNUCLIDEBONELIVERTABLE2-8A,VALUES-LIQUID*EMERGENCY CONDENSER VENTADULTmrem-mlhr-pCiTBODYTHYROIDKIDNEY2.27E-12.27E-12.27E-1LUNGGI-TRACT2.27E-12.27E-lCu642.72Mn541.06E-24.37E+3Fe556.58E+24.55E+2Fe591.02E+32.41E+3Co582.88E-38.83E+1Co601.71E-12.56E+2Zn652.31E+47.36E+4Sr892.18E+4Sr905.44E+5Zr952.40E-17.81E-2Mn561.73E-1Mo998.04E+1Na241.34E+21.34E+2I1311.37E+21.96E+2I1332.25E+13.91E+1Ni651.93E-12.50E-2I1324.64E-31.24E-2Cs1342.98E+57.08E+5Cs136Cs1372.96E+41.17E+53.82E+55.22E+5Ba1401.84E+22.32E-lCe1412.21E-21.50E-2Nb95La1404.38E+22.44E+29.90E-24.99E-2Ce1441.174.89E-11.286.868.33E+21.06E-21.30E+31.06E+29'2E+22.04E-32.04E-31.98E+22.88E-32.88E-35.65E+21.71E-11.71E-13.32E+45.87E-34.92E+46.27E+21.34E+55.35E-21.88E-31.22E-13.07E-21.53E+12.20E-11.82E+21.34E+21.34E+21.34E+21.12E+26.43E+43.36E+21.19E+15.75E+36.82E+11.14E-24.34E-34.34E-11.98E-25.79E+55.39E-22.29E+58.42E+49.46E-46.51E+43.42E+58.19E-21.77E+51.21E+11'1E-47.88E-21.78E-39.67E-57.00E-31.31E+29.73E-42.41E+21.32E-21.57E-51.57E-S6.33E-25.45E-42.90E-1Cr513.24E-53.24E-5.1.247.43E-12.74E-11.653.12E+22.32E+29.73E-41.57E-51.48E+63.66E+35.45E-43.95E+21.06E-21.34Ei42.54E+22.61E+26.72E+28.02E+32.88E-31.79E+31.71E-14.81E+35.87E-34.63E+43.50E+31.57E+41.88E-32.42E+25.521.86E+21.34E+21.34E+25.17E+13.51E+16.36E-12.33E-37.61E+41.24E+48.92E+31.33E+45.89E+41.01E+41.33E-13.79E+29.67E-S5.68E+1*Calculated inaccordance withNUREG0133,Section4.3.1;andRegulatory Guide1.109,Regulatory positionC,Section1.004152LL-40-Unit1ODOMRevision14June1994

TABLE3-1CriticalReceptorDispersion Parameters'or GroundLevelandElevatedReleasesELEVATEDELEVATEDGROUNDGROUND'OCATION DIRMILES~Xsecm'i~D~m'gXIIXsecm'y~D~msiResidences DairyCowsfMilkGoats'eat AnimalsGardensSiteBoundaryE(980)SE(1300)SE(130D)ESE(1150)E(974)ENE(674)1.42.62.61.81.80.41~8E-07b2.2E-08'.2E-08'.1E-08'.0E-07'.4E-06~5.2E-097.0E-10'.0E-10'.7E-09'.5E-09'.4E-08'~4.02E-076;00E-086.00E-081.16E-072.53E-076.63'E-06 858E-091.64E-091.64E-093.54E-095.55E-096.35E-08a.Thesevalueswillbeusedindosecalculations beginning inApril1986butmayberevisedperi.odically toaccountforchangesinlocations offarms,gardensorcriticalresidences.

b.Valuesbasedon5yearannualmeteorological data(C.T.Main,Rev.2)c.Valuesbasedon5yearaveragegrazingseasonmeteorologi.cal data(C.T.MainRev.2)d.Valuearebasedonmostrestri.ctive X/Qland-based sector(ENE).(C.T.Mai.n,Rev.2)e.Valuesarebasedonaverageannualmeteorological datafortheyear1985.f.Conservative locationbasedonpastdairycowandgoatmilkhistory.004152LL41Unit1ODCMRevt.sion 13December1993

aTABLE3-2GammaAirandWholeBodyPlumeShineDoseFactors*ForNobleGasesNuclideKr-85Kr-85mKr-87Kr-88Kr-89Kr-83mXe-133Xe-133mXe-135Xe-135mXe-137Xe-138Xe-131mAr-41GammaAirB,meadr~Cisec2.23E-61.75E-31.02E-22.23E-22.50E-22.26E-6a2.80E-42.27E-42.62E-35.20E-32.30E-31.32E-21.74E-S1.64E-2~GammaWholeBodyV,mremIrr~Cisec1.68E-39.65E-32.17E-21.71E-22.41E-41.87E-42.50E-34.89E-32.20E-31'6E-21.47E>>61.57E-2*Calculated inaccordance withRegulatory Guide1.109.(SeeAppendixB.)004152LL-42-Unit1ODCMRevision14June1994

TABLE3-3IMMERSION DOSEFACTORS*Nuc1ideQ~B~od**~L-skin*****gQl-Ai~r***Kr83m7.56E>>02Kr85m1.17E3Kr851.61ElKr875.92E3Kr881.47E4Kr891.66E4Kr901.56E4Xe131m9.15E1Xe133m2.51E2Xe1332.94E2Xe135m3.12E3Xe1351.81E3Xe1371.42E3Xe1388.83E3Ar418.84E31.46E31.34E39.73E32.37E31.01E47.29E34.76E29.94E23.06E27.11E21.86E31.22E44.13E32.69E31~93E11.23E31.72E16.17E31.52E41.73E41.63E41.56E23.27E23.53E23.36E31.92E31.51E39.21E39.30E32.88E21.97E31.95E31.03E42.93E31.06E4783E31.11E31.48E31.05E37.39E22.46E31.27E44.75E33.28E3*From,TableB-l.Regulatory Guide1.109Rev.1**mrem/yrperpci/m3.***mrad/yrperpCi./m~.004152LL-43-Unit1ODCRRevision14June1994

TABLE3-4DOSEANDDOSERATER;VALUES-INHALATION

-INFANT'rem r.pCi/mNUCLIDEH3*C14*Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95Nb95Mo99I-131I133Cs134Cs137Ba140La140Ce141Ce144Nd147BONE2.65E41.97E41.36E41.93E43.98E54.09E71.15E51.57E43.79E41.32E43.96E55.49ES5.60E45.05E22.77E43.19E67.94E3LIVER6.47E25'1E32.53E41.17E42.35E41.22E38.02E36'6E42.79E46.43E31.65E24.44E41.92E47."03E56'2ES5.60E12.00E21.67E41.21E68.13E3TBODY6.47E25.31E38.95E14.98E33.33E39.48E31.82E3118E43.11E41.14E42.59E62.03E43.78E33.23El1.96E45.60E37.45E44.55E42.90E35'5E11.99E31.76E55.00E26.47E25'1E35.75E16.47E25.31E31.32El4.98E33.25E41.48E73.56E63.11E44.72E32.65E25.18E42.24E41.90ES1.72ES1.34E15.25E35.38ES3.15E3THYROIDKIDNEYLUNG6.47E25.31E31.28E41.00E6GI-LLI6.47E25.31E33.57E27.06E37.77E51.11E44.51E63.19E46.47E5514E42.03E66.40E4l.12E71.31E51.75E62.17E44.79E51.35E51.27E4487E41.06E32.16E37.97E41.33E37.13E41.33E31.60E63.84E41.68ES8.48E45.17E5984E63.22E52.16E41.48E53.12E48.69E41.09E31.02E62.48E4*mrem/yrperpci/m~.Thisandfollowing QTablesCalculated inaccordance withNUREG0133,Section5.3.1,exceptC14valuesinaccordance withRegulatory Guide1.109EquationC-8.004152LL44Unit1ODCRRevision14June1994

TABLE3-5DOSEANDDOSERATEQVALUES-INHALATION mremrpCi/mCHILDNUCLIDEH3*C14*Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95Nb95Mo99I131I133Cs134Cs137Ba140La140Ce141Ce144Nd147BONE3.59E44.74E42'7E44.26E45.99ES1.01E81.90E52.35E44.81E41.66E46.51E59.07E5740E46.44E23.92E46.77E6108E4LIVER1.12E36.73E34.29E42.52E43.34E41.77E31.31E41.13E54.18E49.18E31.72E24.81E42.03E41.01E68.25E56.48El2.25E21.95E42.12E68.73E3T.BODY1.12E36.73E31.54E29.51E37.77E31.67E43.16E32.26E4,7.03E41.72E46.44E63.70E46.55E34.26E12'.73E47.70E32.25E51.28E54.33E37.55E12.90E33.61E56.81E21.12E36.73E38.55E11.12E36.73E32.43E11.00E47.14E41.62E73.85E65.96E48.62E33.92E27.88E43.38E43.30E52.82E52.11E18.55E31~17E64.81E3THYROIDKIDNEYLUNG1-12E36.73E31.70E4GI-LLI1.12E36.73E31.08E3158E6229E41-11E52.87E3127E6111E67.07E43.44E47.07E6962E49.95E51.63E42.16E61.67ES1.48E73.43ES1.35E51.27ES2.84E35'8E31.21E53.85E31.04E51.74E61.83E55.44ES3.62E31.02E52.26E55.66E41.20E73.89E53.28E58.21E42.23E66.11E46.14E53.70E4*mrem/yrperpci/m'.004152LL-45-Unit1ODQ4Revision14June1994

TABLE3-6DOSEANDDOSERATER;VALUES-INHALATION mmemrpCi/m'EEN NUCLIDEH3*C14*Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95Nb95Mo99I131I133Cs134Cs137Ba140La140Ce141Ce144Nd147BONE260E43.34E41.59E43.86E44.34E51.08E81.46ES186E43.54E41.22E45.02ES6.70ES5.47E44.79E22.84E44.89E67.86E3LIVER1.27E34.87E35.11E42.38E43.70E42.07E31.51E41.34E54.58E41.03E41.69E24.91E42.05E41.13E68.48E56.70E12'6E21.90E42-02E68.56E3GI-LLI1.27E34.87E31.35E28.40E35'4E31.27E34.87E37.50E11.27E34.87E33.07E11.27E41.27E34.87E32.10E41.27E34.87E33.00E31.98E66.68E41.24ES6.39E31.43E42.78E31.98E46.24E48'4E41.53E61.34E68.72E61.24E61.78E59.52E42.59ES4.66E41.25E46'8E63.15E45.66E33.22E12.64E46.22E35.49ES3.11E53.52E36.26El2.17E32.62E55.13E21~46E72'2E66.74E41.00E44.11E28.40E43.59E43.75ES3.04E52.28E18.88E31.21E6502E32.42E63.71E51.65E77.65ES2.69E67.51ES1.49E59.68E41.54ES2.69ES6.49E31.46E51.21E52.03E6214ES6.14E51.03E49'6E38.48E32.29E5487E51.26E51.34E78.64E53.72ES1.82E5T.BODYTHYROIDKIDNEYLUNG*mrem/yrperpci/m~.004152LL-46-Unit1ODCMRevision14June1994

TABLE3-7DOSEANDDOSERATE'VALUES-INHALATION mremrpCi/mADULT~UC~LIH3*C14*Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr'95Nb95Mo99I131I133Cs134Cs137Ba'40La140Ce141Ce144Nd147BONE1.82E42.46E41.18E43.24E43.04ES9.92E71.07E51.41E42.52E48.64E33.73E54.78ES3.90E43.44E21.99E43.43E65.27E3~LIVE1.26E33.41E33.96E41.70E42.78E41.58E31.15E41.03ES3.44E47.82E31.21E23.58E41.48E48.48E56.21ES4.90E11.74E21.35E41.43E66.10E3TBODY1.26E33.41E31.00E26.30E33.94E31.06E42.07E31'8E44.66E48.72E36.10E62.33E44.21E3230E12.05E44.52E37.28ES4.28ES2.57E34.58E11.53E31.84ES365E21.26E33.41E35.95E11.26E33.41E32.28E19.84E36.90E41.19E72.15E65.42E47.74E32.91E26.13E42.58E42.87ES2.22E51.67E16.26E38.48ES3.56E3~TYROIDKIDNEYLUNG1.26E3GI-LLI1.26E33.41E33.41E31.44E43.32E31.40E67.21E47.74E46.03E31.02E61.88E59.28ES1.06E55'7E6864ES285E55.34E41.40E63.50ES960E61.77E65.05E59.12E47.22ES1.50E51.04E52.48ES6.28E38.88E39.76E41.04E47.52E41.27E68.40E32.18E51.36E54.58ES3.62ES120ES7'8E68'6E52.21ES1.73ES*mrem/yrperpCi/m.004152LL-47-Unit1ODCMRevision14June1994

UCLIDEH3C14Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95Nb95Mo99I131I133Cs134Cs137Ba140La140Ce141Ce144Nd147TABLE3-8DOSEANDDOSERATER;VALUES-GROUNDPLANEALLAGEGROUPSme~mremrpci/secTOTALBODY4.65E61.40E9'.73EB3.80E82.15E107.46E82.16E42.45E8136E83.99E61.72E72.39E66.83E91.03E102.05E71.92E71.37E76.96E78.46E6SKIN5.50E61.64E93.20E84.45E82.53E108.57E82.51E42.85E81.61E84.63E62.09E7291E67.97E91.20E102.35E72.18E71.54E78.07E71.01E7004152LL-48-Unit1ODCMRevision14June1994

TABLE3-9DOSEANDDOSERATER;VALUES-'COWMILK-INFANTgP~mrempCi/secNUCLIDEH3C14'r51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95Nb95Mo99I131I133Cs134Cs137Ba140La140Ce141Ce144Nd147BONE3.23E6LIVER2.38E36.89ES8.43E71.22E83'3E96.93E98.19E103.85E34'1E56.81E88.52E62.51E75.44E72.13E81.39E75.90E71.21E109.39E21.64ES1.04E88.02E81.24E71.21E82.03E12.28E41.49E64.43E21.21ES7.991.39E46.10E5'4.55E22.41E104.49E103.47E104.06E10T.BODY2.38E36.89E58.35E45.68E61.45E78.38E73.46E71.39EB558E91.99E8209E10.6.66E2117E52.03E73.53E83'3E64.54E92.88E96.22E62.061.64E38.34E42'9E1THYROIDKIDNEY2.38E36.89ES545E42.38E36.89ES1.19E45,.56E6LUNG2.38E36.89ESGI-LLI2'8E36.89ES1.06E52.43E69.21E62.66E76.91E66.29E75.87E9101E31.54ES1.55E82.64E119.37E82.'26E92.87E47.42E44.28E32.46ES'176E21.02E83.46E71.40E81.02E101.42EB1'2E94.68ES3.03E83.43E72.86E72.10E61.22E81.27E82.97E79.39E47.18E68.54E7289ES1.46E71.16E104.74E91.09E104.41E9mrem/yrperpci/m~.004152LL-49-Unit1ODCMRevision14June1994

TABLE3-10DOSEANDDOSERATER;VALUES-COWMIL'K-CHILDm~~mremrpci/secNUCLIDEH3C14Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95Nb95Mo99I131I133Cs134Cs137Ba140La140Ce141Ce144Nd147BONE1.65E6LIVER1.57E33.29ES6.97E76.52E72.63E93.64E97.53E102.17E31,86E53.26ES4.04E61.35E73.07E71.06ES6.94E62.89E77.00E94.77E21.03E44.07E73.28ES4.99E65.87E79.701.15E41.04E62.24E25.14E43.395.73E33.26E51.81E21.50E102.45E102.17E102-OSE10T.BODY1.57E33.29E55.27E43.59E61.15E75.26E72.13E78.52E74.35E91.04ES1.91E104.25E25.69E41.01E7186ES1~89E65.18E93.07E93.43E61.148.51E25.55E41.40E11.57E33.29E52.93E41.57E33.29E57.99E33.78E64.41E91.08E119.27ES6.83E21.00ES8.69E75.39ES8.32E67.61E96.78E91.67E42.51E31.80E59.94E1THYROID~IDNEYLUNG1.57E3GI-LLI1.57E32.09E73.06E72.73E92.44E93.07E41.13E7685E61~10ES4.05E71.60E81.23E91.41ES'1.01E94.98E54.42ES3.37E72.92E72.01E61.32ES1.30ES2.97E79'5E47.15E68.49E72.87ES3.29ES3.29E55.34E42.80E6mrem/yrperpci/m~.004152LL-50-Unit1ODCRRevision14June1994

TABLE3-11DOSEANDDOSERATEQVALUES-COWMILK-TEENm~~mremrpci/secNUCLIDEH3C14'r51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95Nb95Mo99I131I133Cs134Cs137Ba140La140Ce141Ce144Nd147BONE6.70ES2.78E72.81E71.34E91.47E94.45E109.34E2186E51.34E81.66E66.49E99.02E92.43E74.054.67E34.22E59.12E1LIVER9.94E2"1.34E59.01E61.97E76.57E74.55E61.86E74'5E92.95E21.03ES2,.24E71.88ES2.82E61.53E101.20E102.98E41.993.12E31.74E59.91ElT.BODY9.94E21.34ES2.58E41.79E6459E62.54E71.05E74.19E72.17E94.21E71.10E102.03E25.69E44.27E61.01E88.59E57.08E94.18E91.57E65.30E-13.58E22.27E45.94EOTHYROIDKIDNEYLUNGGI-LLI9.94E21.34E51.44E49.94E29.94E29.94E2'.49E103.93ES2.97E94.33E21.00E55.12E73.24ES4.94E64.85E94.08E91.01E41.47E31.04E55'2E12.07E71.85E9'1.59E91.55E86.27E72.42ES1.97E91.75E8125E96SOES4.42ES4.01E73.72E72.13E61.90E81.71E82.00E43'5E71.14ES8.91E61.06E83.58E51.34E5-1.35E51.34E54.34E63.69E45.66E32'9E61.85E7125E78.52E6mrem/yrperpCi/m~.004152LL-51-Unit1ODCMRevision14June1994

TABLE3-12DOSEANDDOSERATER;VALUES-COWMILK-ADULTmr~mremrpCi/secNUCLIDEH3C14Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95Nb95Mo99I131I133Cs134Cs137Ba140La140Ce141Ce144Nd147BONE3.63E51.57E71.61E78.71E87.99E83.15E105.34E21.09E57'1E79.09E53.74E94.97E91.35E72.262.54E32.29ES4.74E1LIVER7.63E27-26E45.41E61.08E73.79E72.70E61.1QE72.77E91.71E26.07E41.24E71.06E81.58E68.89E96.80E91.69E41.141.72E39.58E45.48E1T.BODY7.63E27.26E41.48E41.03E62.52E61.45E76'5E62.42E71.25E92.29E77.74E9.1.16E23.27E42.36E66.08E74.82E57.27E94.46E98.83E53.01E-11.95E21.23E43.28EOTHYROIDKIDNEYLUNGGI-LLI7.63E27.26E48.85E3763E27.26E47.63E27.63E27.26E47.26E41~61E61.85E92.69E26.00E42.81E73.47E101.82EB2.32E82.76E62.88E92.31E9'.75E37.99E25.68E43.20E16.04E61.06E79.55E81~66E76.21E6,1.26E85.47E72.06E81.75E91.28E89.11EB5.43E53.69E82.87E72.80E71.42E61.56EB7.68E81.32E89.69E32.77E78,35E46.58E67.74E72.63ES3.26E31~96E43.72E6mrem/yrperpci/m~.004152LL-52-Unit1(XXRRevt.sion 14June1994

NUCLIDEH3C14Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95Nb95Mo99I131I133Cs134Cs137Ba140La140Ce141Ce144Nd147BONE'.23E6 1.10E61.59E64.24E81~48E101.72Ell4.66E29.42E48.17EB1.02E77.23E101.04E111.45E72.4302.74E31.79ES5.32E1LIVER6.33E36.89ES3.01E67.08E52.78E61~67E67.08E61.45E91.13E23.88E41.27E79.63EB1.49E71.35E111.22E111.45E49.59E-11.67E37.32E45.47E1GI-LLI6;33E36.89E56.33E36.89ES1.00E4'.56E36.82E51.89E51.09E64'6E61.67E76.70EB4.24EB4.38E108.04E12.24E42.47E64.23E84.36E61.36E10863E97.48E52.47E-11.96E21.00E43.35EO3.16El2.71E96.33E36.89E51.43E36.67E56.33E36.33E36.89E56.89ES1.28E42.93E51.11E63.46ES8'8E48.21E5133E67.04E81.22E22.78E41.89E71.12E91.75E73.47E101.42E10416E6168E71.23E93.04E82.15E95.65E43.27E74.17E63.44E72.52E63'6EB3.27E103.44E35.14E22.96E42.11E11.32E103.81E83.56E61.13E4862E51.03E73.46E48.91E3TABLE3-13DOSEANDDOSERATEVALUES-GOATMILK-INFANTm~~meempCi/secT.BODYTHYROIDKIDNEYLUNGmrem/yrperpci/m3.004152LL-53-IUnit1ODCMRevision14June1994

TABLE3-14DOSEANDDOSERATER;VALUES-GOATMILK-CHILDHe~mrempCi/secNUCLIDEH3C14Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95Nb95Mo99I131I133Cs134Cs137Ba140La140Ce141Ce144Nd147BONE,1.65E6~ICE4.17E33.29ES9.06ES8.52ES3.15E87.77E91.58E112.62E2505E41.62E64.81ES1.38E68.35E53.47E68.40E85.76E11.96E44,95E66.52E106.24E107.05E66.18E31.161.38E31.25E52.68E14.07E-16.88E23.91E42.17E13.91E83.94E84.84E65.99E64.49E107.37E10T.BODY4.17E33.29E56.34E34.31ES"1.49ES6.86E52.56E61'.02E75.23E82.22E84.01E105.13E11.40E41.22E62.24E82.27E61.55E109.21E94.12E51.37E-11.02E26.66E31.68EOTHYROIDKIDNEYLUNGGI-LLI4.17E33.29E53.52E34.17E34.17E34.17E33.29ES'.29ES3.29E53.36ES1.36E68.91E46.43E39.62E24.54ES2.72E53.99E51.43E65.29E81'1E99.98E62.28E108.19E92'3E107.32E92.01E33.68E33.02E22.16E41.19E1487E61.92E71.48E83.01E82.13E96.01E43.63E74.09E63.50E72.41E63.97E83.91E83.57E61.13E48.59E51.02E73.44E48.25E1185E41.06E7'1.30E116.46E8mrem/yrperpci/m~.004152LL-54-Unit1ODCHRevision14June1994

TABLE3-15DOSEANDDOSERATERiVALUESGOATMILKme~mremrpci/secTEENNUCLIDEH3C14'r51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95Nb95Mo99I131I133Cs134Cs137Ba140La140Ce141Ce144Nd147BONE6.70E5LIVER2.64E31.34E53.61E53.67ES1.61EB3.14E99.36E101.13E22.23E41.61E81.99E61.08E62.56E58.57E55.46E52.23E65.58E83.56El1.24E42.72E62.26E83.38E62.92E64.86E-15.60E25.06E41.09E13.58E32.39E-13.74E22.09E41.19E11.95E104.58E102.71E103.60E10T~BODY2.64E31.34E53ellE32.15E55.97E43.31E51.26E65.03E62.60E88.99E72.31E102.45E16.82E35.19E51.21E81.03E62.13E101.25E101.88E56.36E-24.30E12'2E37.13E-1THYROIDKIDNEYLUNGGI-LLI264E31.34E51.73E32.64E31.34ES6.82E23.23ES'3.57E82.64E32.64E31.35E54.44E31.62ES2.70ES1.34E55.23ES2.22E61.11ES2.03E67.53E62.91E72'6E85.23E11.20E46.23E66.59E103.89E84.72E85.93E63.74E82.63E98.22E45.30E74.87E64.47E72.56E61.21E31.76E21.25E46.99EO2.41E34.50E61~37E41.07E61.27E74.29E41.46E105.56E95.70E81.23E104.76E95.12E8mrem/yrperpci/m~.004152LL-55-Unit1ODCMRevision14June1994

NUCLIDEH3C14Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95Nb95Mo99I131I133Cs134Cs137Ba140La140Ce141Ce144Nd147BONE3.63E5LIVER2.03E37.26E42.04ES2.10E51.05ES1.70E96.62E106.45E11.31E48.89E71.09E66.50ES1~41E54.95E53'5E51~32E63.33ES2.07E17.29E31.51E61.27E81.90E61.62E62.71E-13.06E22.75E45.69EO2.03E31.36E-l2.07E21.15E46.57EO1.12E102.67E101.49E102.04E10T.BODYTHYROIDKIDNEY2.03E37.26E43.92E21.93ES2.03E37.26E42.03E37.26E41.78E3'.06E31.24E53.28E41.90ES7.27E52.91E61.51ES4.89E71.63E101.40E13.92E32.87ES7.29E7579ES2.18E101.34E101.06E53.61E-22.34E1148E33.93E-12.23ES3.25E17.21E33.41E64.17E102.18ES3.31E68.63E96.93E96.91E22.79ES9.60E16.82E33.84EOTABLE3-16DOSEANDDOSERATER;VALUES-GOATMILK-ADULTm~~mremrpci/secLUNG2.03E3GI-LLI2.03E37.26E47.26E42.36E37.SSE44.48E51.99E6807E42.86E92.30E91.16E31.71E64.67ES3.95E83.33E61.00E47.90E59.30E63.15E41.38E51.65E66.58E62.48E72.10E82'3ES1.91E96.56E44.42E73.49E63.36E7mrem/yrperpci/m~.004152LL-56-Unit1GXtfRevision14June1994

TABLE3-17DOSEANDDOSERATER;VALUES-COWMEAT-CHILDm~~mremrpci/secNUCLIDEH3C14Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95Nb95Mo99I131I133Cs134Cs137Ba140La140Ce141Ce144Nd147BONE5'9E52.89ES2.04EB2.38ES2.65ES7.01E91.51E64.10E64.15E69.38E-26.09ES8.99EB2.20E72.80E-21.17E41.48E65.93E3LIVER2.34E21.06ES5.15E61.53ES3.30ES9.41E64.64E76'5EB3.32E51.59E65.42E44.18E61.16E-11.00E98.60EB1.93E49.78E-35.82E34.65E54.80E3T.BODY2.34E21.06E54.55E31.37E64.74E71.65EB2.88E71.37ES3.95ES7'7E61.78E9295ES1'4E61.34E42.37E64.39E-22.11ES1.27EB1.28E63'0E-38.64E27.91E43.72E22.34E21.06E52.52E32.34E21.06E56.90E21.44E64OOES1.38E92.15E14.75E51.50E61.16ES6.86E61.93E-13.10ES2.80ES6.27E32.55E32.57E52.64E3THYROIDKIDNEYLUNGGI-LLI2.34E22.34E21'6ES1.06ES1.15E41.11E72e73E27.26E61.21EB7.61E64.61E32.41ES4.32E68.66E72'4E79.58E73.44EB5.49E72'7ES1.12EB1.03E79.44E73.46EB2.95E94.48E43.72E54.67E-21.11EB5.39E61.01ES5.39E6mrem/yrperpci/m~.004152LL-57-Unit1ODCRRevision14June1994

TABLE3-18DOSEANDDOSERATERIVALUES-COWMEAT-TEENm'-~remlrrr pci/secNUCLIDEH3C14Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95Nb95Mo99I131I133Cs134Cs137Ba140La140Ce141Ce144Nd147BONE2.81ES1.50ES1.15ES1.59ES1.40ES5.42E98.50ES2.37E62.24E65.05E-23.46E84.88E81.19E71.53E-26.19E37.87ES3.16E3LIVER1.94E25.62E4450E61.07E82.69ES805E63.90E75.52ES2.68E51.32E63.90E43.13E68.57E-28.13ES6.49ES1.46E47.51E-34.14E33.26ES3.44E3T.BODY1.94E25.62E42.93E38.93E52.49E71.04ES1.86E78'OE72.57ES4.01E61.34E91.84E57.24ES7.43E31.68E62.61E-23.77ES2.26ES7.68E52.00E-34.75E24.23E42.06E21.94E25.62E41.62E31.94E25.62E46.39E21.34E63.53ES9.15E8120E13.94ES1.28E68.92E45.40E61.50E-12.58ES2.21E84.95E31.95E31.94ES2.02E3THYROIDKIDNEYLUNGGI-LLI1.94E21.94E25.62E45.62E46.77E78.47E79.87E78.58E79.81E39.24E64.62E76.36E81.11E85.09E82.34ES1.67E71.52ES6.19ES5.63E96.98E4620E5648E-21.01E79.24E61.84E74.31E21.18E71.98E81.24E74.16E34.90E5mrem/yrperpci/m~.004152LL-58-Unit1ODCMRevision14June1994

TABLE3-19DOSEANDDOSERATER;VALUES-COWMEAT-ADULTm~~meemrpci/secNUCLIDEH3C14'r51Mn54Fe55Fe59Co58BONE3.33E51.85E81.44ESLIVER3.25E26.66E45.90E61.28ES3.39E81.04E7T.BODY3.25E26.66E43.65E31.13E62.98E7130ES2.34E73.25E26.66E42.18E33.25E26.66E48.03E21.76E6THYROIDKIDNEYLUNGGI-LLI3.25E2325E26.66E46.66E44.84E39.17E57.14E71.81E77.34E79.46E7113E92.12ESCo60Zn65Sr89Sr90Zr95Nb95Mo99I131I133Cs134Cs137Ba140La140Ce141Ce144Nd1472.26E81.66ES8'8E91~06E63.04E62.69E66.04E-24.35ES5.88E81.44E71~86E-27.38E39'3E53.59E37.19E83.40E51~69E64.71E43.85E61.05E-11.03E98.04E81.81E49.37E-34.99E33.90E54.15E33.25ES4.76E62.06E92.30E59.08ES8.97E32.21E63.20E-28.45ES5.26ES9.44ES2.48E-35.66E25'1E42.48E25.03E71.11E8l.26E91.54E14.81ES5.34ES1.67E61.07ES6'1E61.83E-13.35ES2.73E86.15E32.32E32'1ES2.42E31.11E89.07E71.04E49.45ES453ES2.66E72.42E81.08E91.03E101.09ES1.02E69.44E-21.81E71.56E72.97E76.88E21.91E73.16ES1.99E7mrem/yrperpci/m~.004152LL-59-Unit1ODCMRevision14June1994

RlTABLE3-20DOSEANDDOSERATEVALUES-VEGETATION m'~modempCi/secCHILDNUCLIDEH3C14Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95Nb95Mo99I131I133Cs134Cs137Ba140La140Ce141Ce144Nd147BONE3.50E6LIVE4.01E37.01E57'3ES3.97ES8.12ES3.59E101.24E123.86E61.02E67.16E71.69E66.65ES4.05ES6.42ES6.45E73.78E82.16E98.50ES3.99E57.70E67.20E72.09E62.77ES3.25E36.56E51.27E87.23E42.43ES1.13E33.27ES3.98E7586E41.60E102.63E102.39E102.29E10T.BODY4.01E37'1E51.17E51.77E81.25E83.20ES1.97ES1.12E91~35E91.03E93.15Ell7.56E52.85E51.91E64.09E77.92E55.55E93.38E91.62E73.83E24.85E46.78E64.54E3THYROID4.01E37.01E56.49E42.38E103'9ESKIDNEY4.01E37.01E51.77E41.86ES1.36E91.22E63.75E51.65E71.18ES3.49E68.15E97.46E97.90E41.43ES2.21E73.22E4LUNG4.01E3GI-LLI4.01E32.68E91.45ES1.43E81.40E83.16E74.08E81.04E109.28E77.01E57.01E51.18E56.20E65.58E82.29E87.50E71.86ES6.69ES3.76E82.10E93.80ES1.39E91.67E108.86ES737ES6.37E66.41E68.44ES2.93E91.42E8mrem/yrperpci/m~.004152LL-60-Unit1ODCMRevision14June1994

TABLE3-21DOSEANDDOSERATEVALUES-VEGETATION me~mremrpci/secTEENNUCLIDEH3C14Cr51Mn54Fe55Fe59Co58Co60Zn65Sr89Sr90Zr95Nb95Mo99I131I133Cs134Cs137Ba140La140Ce141Ce144Nd147BONE1.45E63.10ES1.79ES4.24ES1.51E107.51E111.72E64.80ES3.85E79.29E57.10E91~01E101.38ES1.81E32'3E55.27E73.66E4LIVER259E3291E54.54E8220E84.18E84.37E72.49ES1.47E95.44E52.66ES5.64E65.39E71.58E61.67E101.35E101.69ESS.SSE21.89ES2.18E73.98E4T.BODY2.59E32.91E56.16E49.01E75.13E71.61E81~01ES5.60ES6.86E84.33ES1.85E113.74E51.46E51~OSE62'9E74SOES775E94.69E98.91E62.36E22.17E42.83E62.3863THYROID2.59E32.91E53.42E4KIDNEY2.59E32.91E51.35E41.36E8941ES2.20ES2.76E65.31E94.59E95.74E48.89E41.30E72.34E47.99E52.58ES1.29E71.57E109.28E7LUNG2.59E32.91E58.79E41.40E81.32E82.03E91.78E9GI-LLI2.59E32.91E51.03E79.32ES9.53E79.89ES6.02ES3.24E96.23ES1.80E92.11E101.26E91.14E91.01E71.07E71.19E62OSES1.92ES1.14E52.13ES5.10E75,40ES.1.33E101.44E8mrem/yrperpci/m'004152LL-61-Unit1ODCMRevision14June1994

R,TABLE3-22DOSEANDDOSERATEVALUES-VEGETATION mam@emrpci/secADULTNUCLIDEH3C14Cr51Mn54Fe55~Fe59Co58Co60Zn65Sr89Sr90Zr95Nb95Mo99I131I133Cs134Cs137Ba140La140Ce141Ce144Nd147BONE8.97E52.00E81.26E83.17E89.96E96.05E111.18E63.55E5404E71.00E64.67E96.36E91.29E81.98E31.97E53.29E73.36E4LIVER2.26E31.79ES3.13ES1.38ES2.96ES3.08E7T.BODY2.26E31.79ES4.64E45.97E73.22E71.13E86.90E71.01E93.77E51.98E56.14E65.78E71.74E61.11E108.70E91.61ES9.97E21.33ES1.38E73.88E44.56ES2.86ES1.48E112.55E51.06ES1.17E63.31E75.30E59.08E95.70E98.42E62.63E21.51E41.77E62.32E31.67E8'.69ESTHYROIDKIDNEY'.26E31.79E52.77E42.26E31.79E51.02E49.31E76.75ES2.56ES3.03E63.59E92.95E95.49E46.19E48.16E62.27E4-/5.92ES1.95ES1.39E71.90E109.91E7LUNGGI-LLI2.26E32.26E31.79ES6.15E47.69E78.27E71.79ES1.17E79.58E87'1E71.02E9624ES3.14E96'6ES1.60E91.75E101.20E91.20E91.42E71.53E71.56E61.19E91.94E89.81E81.68ES9.25E42.65E87.32E75.09ES1.11E101.86E8mrem/yrperpci/m~004152LL-62-Unit1QXRRevision14June1994

TABLE3-23PARAMETERS FORTHE.EVALUATION OFDOSESTOREALMEMBERSOFTHEPUBLICFROMGASEOUSANDLIQUIDEFFLUENTS P~athwaFishFishShoreline Parameters U(kg/yr)-adultD~~(mrem/pCi)

U(hr/yr)-adult-teenValue21EachRadionuclide 6767Reference Reg.Guide1.109TableE-5Reg.Guide1.109TableE-11Reg.Guide1.09AssumedtobesameasAdultShoreline D~EachRadionuclide (mrem/hrperpCi/m~)Reg.Guide1.109TableE-6Inhalation DFA-EachRadionuclide Reg.Guide1..109TableE-7004152LL-63-Unit1ODCMRevt.sion 14June1994

NINEMILEPOINTNUCLEARSTATIONRADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAMSAMPLINGLOCATIONS TABLE5.1TypeofRadioiodine andParticulates (air)Radioiodine andParticulates (air)Radioiodine andParticulates (air)Radioiodine andParticulates (air)Radioiodine andParticulates (air)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation.

(TLD)DirectRadiation (TLD)DirectRadiation (TLD)*MapLin1012131415161718IIcin'nvPrrmNNineMilePointRoadNorth(R-1)Co,Rt.295LakeRoad(R-2)Co,Rt.29(R-3)VillageofLycoming, NY(R-4)MontarioPointRoad(R-5)NorthShoreline Area(75)NorthShoreline Area(76)NorthShoreline Area(77)NorthShoreline Area(23)PJAFEastBoundary(78)Rt.29(79)Rt.29(80)MinerRoad(81)MinerRoad(82)LakeviewRoad(83)LakeviewRoad(84)SiteMeteorological Tower(7)EnergyInformation Center(18)Lin1.8miI88oE1.1miI104ESE1.5miI132oSE1.8miI143oSE16.4miI42oNE0.1rnlI5oN0.1miI25oNNE0.2miI45oNE0,8miI70oENE1.0miI90oE1.1mi@115oESE1.4miI133oSE1.6miI159'SE1.6miI181'1.2miI200SSW1.1miI225oSW0.7miI250WSW0.4miI265oW*Map=SeeFigures5.1-1and5.1-2004152LL-64-Unit1ODC8Revision14June1994

NINEMILEPOINTNUCLEARSTATIONRADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAMSAMPLINGLOCATIONS TABLE5.1(Continued)

TypeofI*MapLinEnv.PrrmNDirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)DirectRadiation (TLD)SurfaceWaterSurfaceWater19NorthShoreline (85)20'orthShoreline (86)21222324252627282930313233343536373839NorthShoreline (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)W.Boundary, BibleCamp(15)LakeRoad(98)OSSInletCanal(NA)JAFNPPInletCanal(NA)0.2miI294~WNW0.1miI315oNW0.1mi5341'NW4.5miI97'4.1miI111oESE4.2miI135~SE4,8mi@156SSE4.4miI183~S4.4miI205SSW4.7miI223oSW4.1mi5237oWSW19.8miI163~S12.6miI226oSW3.6mi5199SSW3.1mi@220~SW1.8miI143oSE5.3miI123oESE0.9miI237WSW1.2miI101~E7.6miI235~SW0.5miI70~ENE(NA)=Notapplicable

• IVlap=SeeFigures5.1-1and5.1-2004152LL-65-Unit1ODC8Revision14June1994

NINEMILEPOINTNUCLEARSTATIONRADIOLOGICAL ENVIRONMENTAL IVIONITORING PROGRAMSAMPLINGLOCATIONS TypeofSamleTABLE5.1(Continued)

• MapLocationCollection SiteEnv.ProramNo.LocaionShoreline SedimentFishFishFishMilkMilkMilkMilkMilkMilkMilk(CR)FoodProductFoodProduct40424344454764656673.4849SunsetBayShoreline (NA)NMPSiteDischarge Area(NA)NMPSiteDischarge Area,(NA)

OswegoHarborArea(NA)MilkLocation¹50MilkLocation¹7MilkLocation¹65MilkLocation¹55MilkLocation¹60MilkLocation¹4MilkLocation(Woodworth)

ProduceLocation¹6++(Bergenstock)

(NA)ProduceLocation¹1++(Culeton)

(NA)1.5miI80oE0.3miI315~NW(and/or)0.6miI55'E6,2miI235~SW82miI93oE5.5miI107'SE17.0mi@220SW90mio95'95mio90oE7.8miI113~ESE139miI234SW1.9miI141~SE1.7m)@96oEFoodProductFoodProductFoodProduct505152ProduceLocation¹2++(Vitullo)

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

(NA)ProduceLocation¹3++(C.Narewski)

(NA)1.9miI101oE1.5rniI114oESE1,6mio84o E*Map=++(NA)TheJonesmilklocationhasbeendeletedduetotheherdbeingsold.(Maplocation¹46.)SeeFigures5.1-1and5.1-2FoodProductSamplesneednotnecessarily becollected fromalllistedlocations.

Collected sampleswillbeofthehighestcalculated siteaverageD/Q.Notapplicable ControlResult(location) 004152LL-66-Unit1ODCMRevision14June1994 e

NINEMILEPOINTNUCLEARSTATIONRADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAMSAIVIPLING LOCATIONS TABLE5.1(Continued)

TypeofIFoodProductFoodProduct(CR)FoodProduct(CR)FoodProductFoodProductFoodProduct*MapLoi535455565758IIiniEnv.PrrProduceLocation¹4++(P.Parkhuist)

(NA)ProduceLocation¹7++(McMillen)(NA)ProduceLocation¹8'Denman)(NA)ProduceLocation¹9(O'onnor)

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

(NA)Lin2.1miI110ESE15.0miI223'W12.6miI225SW1.6mi@171~S2.2miI123ESE2.0miI112ESEFoodProductFoodProduct(CR)59ProduceLocation¹12(Barton)(NA)60ProduceLocation¹13'(Flack)(NA)1.9miI115ESE15.6miI225oSWFoodProductFoodProductFoodProduct616263ProduceLocation¹14(Koeneke)

(NA)ProduceLocation¹15(Whaley)(NA)ProduceLocation¹16(Murray)(NA)1.9miI95~E1.7miI136~SE1.2miI207~SSW*Map++(NA)SeeFigures5.1-1and5.1-2FoodProductSamplesneednotnecessarily becollected fromalllistedlocations.

Collected sampleswillbeofthehighestcalculated siteaverageD/Q.Notapplicable ControlResult(location) 004152LL-67-Unit1ODCHRevision14June1994 0

FIGURE5.1-1004152LLUnit1(XX'evision 14June1994

FIGURE5.1-2004152LL-69-Unit1ODQ4Revision14June1994

~domfsSOI?IdellCALEOFMILESLEGENDInterstate~

.UN.4Staletttahwaya...

CovolyReacts,,TownRoacts..............

Covalylines.TowoLtast City4VNaeoLines......

Itaitloacta.

EttyIRosoENfALsueLE...........Q LOCATIOttFIGURE5.1-2NINEMILEPOINTOFF-SITEMI-"IP(12/93)talxvae4F?O'N.tslCOvae74'yyW.llOIveyOCOvaty SacgOlcretrasty.talesArse944octavelrnes496ISteeralSteelisatltotraplLAKEON7ARIO422Xl51I63IoeRSuch6444Illecicoyvtv~ca3392~rrclsl~slyceslsllc IscIconlReichII~cyvccrnyelsctaAlakeIIC<<l<<vcrcllnll~~Plll<<ccllrl~cnlulclvep~allP~Ivcrvw/Srvovouy~<<eDl0orevr<<lvcclu~K~0Gy51%<<vvn)IItarnccgXSKSSCorcvrs3teQQI8ANEWSeven<<CI~lsoaYESleerayAvtaaICometN66II~II1l.MvvvIIMoxlco'IgOlEcXIa<Mls

Ce<<eeIaroe7~IVI3l0~ja~I<<Ore-%5'OvegoCeesee5ws5e1neI'eorrl<<e

~NeI(isu0~I~OIIIC!/lje~Mee~'1L1arette>eIv'Nee.sS,Ii~11i/.Iv'Q/jeroeale11AIMIIAL6RMe')~-'-'IIyPj..'he.~~~eall<<g-eey>..V-'~11Sacer'sCseserlIIIItsf~oVIeelsHnnnlbnl~CN$NIjjeoaer8AI.IIeSISMg>>1FULTOLIja'eejoaseeeae I~r~MMnre1I~IIII~I0eja<<elONeNVN~1Y/IIIIA~aICeeeeeeatM.I~I1sensesCareersnvaeakoa~1janCor<<en/~1IISesjPaeeeeeeo IyHsereCes~I//CeeMrsciC<<IMe'1'1eeaeejeoj CeeejerssssnRANejII~1I;'"I~<<vs<<re~IIVIeeSSLlj$l~e~II~eeeIelIICASVGAIllnoserea~SerenejasseeajtoÃ1.JjljC(WNYveerPkn4seesees<<osroSeeeln~o5~IIIV~Isg'wIeaR'MINIIMr&eee<<llear~I~IweaNee~NMV<<IVInn~I'SeeceoI'ICjIjMe<<eNI1ONOSSDAGA COUSSTYtoSaeecearNoeeO~~olejvS20M79

FIGURE5.1.3-1004152LL-70-Unit1ODCMRevision14June1994

lPO~i(y~lt~0'r

APPENDIXALIQUIDDOSEFACTORDERIVATION 004152LL-71-Unit1ODCRRevision14June1994

AppendixALiquidEffluentDoseFactorDerivation, AA(mrem/hrperpCi/ml)whichembodiesthedoseconversion factors,pathwaytransferfactors(e.g.,bioaccumulation factors),

pathwayusagefactors,anddilutionfactorsforthepointsofpathwayorigintakesintoaccountthedosefromingestion offishanddrinkingwaterandthesediment.

Thetotalbodyandorgandoseconversion factorsforeachradionuclide willbeusedfromTableE-11ofRegulatory Guide1.109.Toexpeditetime,thedoseiscalculated foramaximumindividual insteadofeachagegroup.Themaximumindividual dosefactorisacomposite ofthehighestdosefactorAofeachnuclideiagegroupa,andorgant,henceA,.Itshouldbenotedthatthefishingestion pathwayisthemostsig'nificant pathwayfordosefromliquideffluents.

Thewaterconsumption pathwayisincludedforconsistency withNUREG0133.Theequationforcalculating dosecontributions giveninsection1.3requirestheuseofthecomposite dosefactorA;,foreachnuclide,i.Thedosefactorequationforafreshwatersiteis:-X)t~-X,t~)(DFL)%+eeeD>>+69.3DWee(3-e'(DSS),)-S,t-3,eb(D.)(3i)Where:KoUIsthedosefactorfornuclidei,agegroupa,totalbodyororgant,forallappropriate

pathways, (mrem/hrperpCi/ml).Istheunitconversion factor,1914E5~1E6pCi/pCi x1E3ml/kg-:-8760hr/yr.Waterconsumption (1/yr);fromTableE-5ofReg.Guide1.109.U/Fishconsumption (Kg/yr);fromTableE-5ofReg.Guide1.109.U,(BF)~SedimentShoreline Usage(hr/yr);fromTableE-5ofReg.Guide1.109.Bioaccumulation factorfornuclidesisinfishs(pCi/kgperpCi/1),fromTableA-1ofReg.Guide1.109.(DFL)~(DFS)iDoseconversion factorforage,nuclidesisgroupa,totalbodyororgant,(mrem/pCi)s fromTableE-11ofReg.Guide1.109.Doseconversion factorfornuclideiandtotalbody,fromstandingoncontaminated ground(mern/hrperpCi/m~);fromTableE-6ofReg.Guide1.109.DDilutionfactorfromthenearfieldareawithinone-quarter mileofthereleasepointtothepotablewaterintakefortheadultwaterconsumption.

ThisistheMetropolitan WaterBoard,OnondagaCountyintakestructure locatedwestoftheCityofOswego;(unitless).

004152LL-72-Unit1ODCMRevision14June1994

AppendixA(Cont'd)D,69.3Dilutionfactorfromthenearfieldarea,withinone,quartermileoftherel'easepointtotheshoreline deposit(takenatthesamepointwherewetakeenvironmental samples1.5miles;unitless).

conversion factor.693x100,100~K,(L/kg-hr)

• 40*24hr/day/.693 inL/m~-d,andK,=transfercoefficient fromwatertosedimentinL/kgperhour.Averagetransittimerequiredforeachnuclidetoreachthe'point ofexposureforinternaldose,itisthetotaltimeelapsedfromreleaseofthenuclidestoeitheringestion forwater(w)andfish(f)orshoreline deposit(s),(hr).Lengthoftimethesedimentisexposedtothecontaminated water,nominally 15yrs(approximate midpointoffacilityoperating life),(hrs).decayconstantfornuclidei(hr').Shorewidthfactor(unitless) fromTableA-2ofReg.Guide1.109.ExampleCalculation ForI-131ThyroidDoseFactorforanAdultfromaRadwasteliquideffluents release:(DFS))(DFL)4,BF,U/DD,U,W2.80E-91.95E-315214012120.35.5mrem/hrperpCi/m~mrem/pcipCi/KgperpCi/Lt<Kg/yrtunitlessUunitlessKohr/yr30hrs.(w~water)24hrs.(f~fish)1.314EShrs.(5.48E3days)730L/yr1.14ESCiCimlk(hr/Yr)3.61E-3hr'rs (s=Shoreline Sediment)

ThesevalueswillyieldanA.Factorof6.79E4mrem-mlperpCi-hraslistedinTable2-4.ItshouldbenotedthatonlyalimitednumberofnuclidesarelistedonTables2-1to2-8.Thesearethemostcommonnuclidesencountered ineffluents.

Ifanuclideisdetectedforwhichafactorisnotlisted,thenitwillbecalculated andincludedinarevisiontotheODCM.Inaddition, notalldosefactorsareusedforthedosecalculations.

Amaximumindividual isused,whichisacomposite ofthemaximumdosefactorofeachagegroupforeachorganasreflected intheapplicable chemistry procedures.

004152LL-73-Unit1ODCRRevision14June1994

APPENDIXBPLUMESHINEDOSEFACTORDERIVATION 004152LL-74-Unit1ODOMRevision14June1994

APPENDIXBForelevatedreleasestheplumeshinedosefactorsforgammaair(B;)andwholebody(V~)garecalculated usingthefiniteplumemodelwithanelevation abovegroundequaltothestackheight.Tocalculate theplumeshinefactorforgammawholebodydoses,thegammaairdosefactorisad)ustedfortheattenuation oftissue,andtheratioofmassabsorption coefficients betweentissueandair.Theequations areasfollows:.GammaAirB,E,R8V,Where:K'onversion factor(seebelowforactualvalue).massabsorption coefficient (cm~/ggairforBtissueforV,)E=Energyofgammarayperdisintegration (Mev)V,averagewindspeedforeachstability class(s),R=downwinddistance(siteboundary, m)8=sectorwidth(radians) s=subscript forstability classI,=IfunctionI,+kI~foreachstability class.(unitless, seeRegulatory Guide1.109)Fractionoftheattenuated energythatisactuallyabsorbedinair(seeRegulatory Guide1.109,seebelowforequation)

W~holeBodV,Patd1.11SB,eWhere:t~=tissuedepth(g/cm~)S.=shielding factorfromstructures (unitless) 1.11=Ratioofmassabsorption coefficients betweentissueandair.Whereallotherparameters aredefinedabove.'K=conversion factor[3.7E10midis1.6E<<6ercr]Ci-sec[1293g]mMev[100~er]g-rad.46~k~~PdWhere:p~massattenuation coefficient (cm/g;airforB~,tissueforV,)p,=definedabove004152LL-75-Unit1ODCRRevision14June1994

APPENDIXB(Cont'd)Therearesevenstability classes,AthruF.Thepercentage oftheyearthateachstability classoccursistakenfromtheU-2FSAR.Fromthisdata,aplumeshinedosefactoriscalculated foieachstability classandeachnuclide,multiplied byitsrespective fractionandthensummed.Thewindspeedscorresponding, toeachstability classare,also,takenfromtheU-2FSAR.Toconfirmtheaccuracyofthesevalues,anaverageofthe12monthwindspeedsfor1985,1986,1987and1988wascomparedtotheaverageoftheFSARvalues.Theaveragewindspeedoftheactualdataisequalto6.78m/s,whichcomparedfavorably tothe.FSARaveragewindspeedequalto6.77m/s.Theaveragegammaenergieswerecalculated usingaweightedaverageofallgammaenergiesemittedfromthenuclide.Theseenergiesweretakenfromthehandbook"Radioactive DecayDataTables",DavidC.Kocher.Themassabsorption (p,)andattenuation (p)coefficients werecalculated bymultiplying themassabsorption (p,/p)andmassattenuation (p/p)coefficients givenintheRadiation HealthHandbookbytheairdensityequalto1.293E-3g/ccorthetissuedensityof1g/ccwhereapplicable.

Thetissuedepthis5g/cm~forthewholebody.Thedownwinddistanceisthesiteboundary.

004152LL-76-Unit1ODCRRevision14June1994

SAMPLECALCULATION Ex.Kr-89APPENDIXB(Cont'd)FSTABILITY CLASSONLY-GammaAir-DATAEPEPea,K=.46VF5.55m/seckEE~=.871PER=644m2.22MeV2.943E-3m'5064E-3m)

.3919m.......vertical plumespreadtakenfrom"Introduction toNuclearEngineering",

JohnR.LaMarsh-IFunctionUc,EE1)EEBi.06.33.45I>+kIz~33+(~871)(~45)~72dis.0.46Ci-secMevers2.943E-3m'.22Mev

.72(mQ)(g/m')(ercrs)(5.55m/s)(.39)(644m)(g-rad)1.55(-6)rads3600shr24hd365dCi/s(~1E6Ci.)Ci1E3mradrad2.76(-2)meadrpCi/sec<<(.0253cm~/g)(Sg/cm~)1.11(.7)2.76(-2)prado][e)pCi/secJ1.89(-2)meadrpci/secNOTE:Theabovecalculation isfortheFstability classonly.ForTable3-2andprocedure values,aweightedfractionofeachstability classwasusedtodetermine theB<andV>values.004152LL-77-Unit1ODCRRevision14June1994 0

APPENDIXCDOSEPARAMETERS FORIODINE131and133,PARTICULATES ANDTRITIUM004152LL-78-Unit1ODQ4Revision14June1994 0

APPENDIXCDOSEPARAMETERS FORIODINE131AND133gPARTICULATES ANDTRITIUMThisappendixcontainsthemethodology whichwasusedtocalculate theorgandosefactorsforI-131iI133@particulates, andtritium.Thedosefactor,Q,wascalculated usingthemethodology outlinedinNUREG-0133.

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

Washoutwascalculated anddetermined tobenegligible.

gvalueshavebeencalculated fortheadult,teen,childandinfantagegroupsforallpathways.

However,fordosecompliance calculations, amaximumindividual isassumedthatisacomposite ofhighestdosefactorofeachagegroupforeachorganandpathway.Themethodology usedtocalculate thesevaluesfollows:C.lInhalation Pathwawhere:K'BR)~(DFA)g,Q(I)dosefactorforeachidentified radionuclide ioftheorganofinterest(units=mrem/yrperpci/m~)iK'constant'f unitconversion, 1E6pCi/pCi(BR),Breathing rateofthereceptorofagegroupa,(units~m~/yr);(DFA)6,Theinhalation dosefactorfornuclidei,organandagegroupa,andorgant(units~mrem/pci)

.Thebreathing rates(BR),forthevariousagegroups,asgiveninTableE-5ofRegulatory Guide1.109Revision1,aretabulated below.AeGrouaBreathinRatem~rInfantChildTeenAdult1400370080008000Inhalation dosefactors(DFA)>forthevariousagegroupsaregiveninTablesE-7throughE-10ofRegulatory Guide1.109Revision1.004152LL-79-Unit1ODCMRevision14June1994

APPENDIXC(Cont'd)C.2R;(G)GroundPlanePathwa-l,tK'KSFDFGl>>eWhere:Q(G)K'osefactorforthegroundplanepathwayforeachidentified radionuclide ifortheorganofinterest(units~m~-mrem/yr perpci/sec)Aconstantofunitconversion, 1E6pCi/pCiAconstantofunitconversion, 8760hr/yearTheradiological decayconstantforradionuclide i,(unitssec')tTheexposuretime,sec,4.73E8sec(15years)(DFG)~Thegroundplanedoseconversion factorforradionuclide ig(units~mrem/hrperpCi/m~)SFTheshielding factor(dimensionless)

Ashielding factorof0.7isdiscussed inTableE-15ofRegulatory Guide1.109Revision1.Atabulation ofDFG,valuesispresented inTableE-6ofRegulatory Guide1.109Revision1.004152LL-80-Unit1ODCRRevision14June1994

APPENDIXC(Cont'd)C.3Grass-CoworGoat-MilkPathwaRi(C)~K'FrDFL~ff+(~fg,)(ee-1)ti,-l,iti+")Y,Where:Ei(C)K'osefactorforthecowmilkorgoatmilkpathway,foreachidentified radionuclide ifortheorganofinterest, (units~m2-mrem/yr perpci/sec)Aconstantofunitconversion, lE6pCi/pCiY,(DFL)LiThecow'sorgoat'sfeedconsumption rate,(units=Kg/day-wet weight)Thereceptor's milkconsumption rateforagegroupa,(units=liters/yr)

Theagricultural productivity byunitareaofpasturefeedgrass,(units=kg/m2)Theagricultural productivity byunitareaofstoredfeed,(units=kg/m2)Thestableelementtransfercoefficients, (unitspCi/liter perpci/day)Fractionofdeposited activityretainedoncow'sfeedgrassTheingestion dosefactorfornuclidei,agegroupa,andtotalbodyororgant(units~mrem/pCi)

Theradiological decayconstantforradionuclide i,(units=sec

-1)Thedecayconstantforremovalofactivityonleafandplantsurfacesbyweathering equalto5.73E-7sec-1(corresponding toa14dayhalf-life)

Thetransport timefrompasturetocoworgoat,tomilk,toreceptor, (units=sec)Thetransport timefrompasture,toharvest,tocoworgoat,tomilk,toreceptor(units~sec)004152LL-81-Unit1CMXttRevision14June1994

APPENDIXC(Cont'd),.Fractionoftheyearthatthecoworgoatisonpasture(dimensionless)

Fractionofthecowfeedthatispasturegrasswhilethecowisonpasture(dimensionless)

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

Thevalueoff,is0.5basedon6monthgrazingperiod.Thisvalueforf,wasobtainedfromtheenvironmental group.TableC-1containstheappropriate valuesandtheirsourceinRegulatory Guide1.109Revisionl.Theconcentration oftritiuminmilkisbasedontheairborneconcentration ratherthanthedeposition.

Therefore, theRz(C)isbasedonX/Q:+(C)~K'K~QP~(DFL)~

075(05/H)Where:%(C)Dosefactorforthecoworgoatmilkpathwayfortritiumfortheorganofinterest, (units=mrem/yrperpci/m~)H0.75o.sAconstantofunitconversion, 1E3g/kgAbsolutehumidityoftheatmosphere, (units~g/m')ThefractionoftotalfeedthatiswaterTheratioofthespecificactivityofthefeedgrasswatertotheatmospheric waterOthervaluesaregivenpreviously.

AsitespecificvalueofHequalto6.14g/m~isused.Thisvaluewasobtainedfromtheenvironmental groupusingactualsitedata.004152LL-82-Unit1ODCMRevision14June1994

APPENDIXC(Cont'd)C.4Grass-Cow-Meat Pathwag(C)~K'FrDFL[~ff+l)+(~1-ff)(ee-l,)tbY,Q(M)Dosefactorforthemeatingestion pathwayforradionuclide iforanyorganofinterest, (units~m~-mrem/yr perpci/sec)Thestableelementtransfercoefficients, (units=pCi/kgperP<</day)Thereceptor's meatconsumption rateforagegroupa,(units~kg/year)Thetransport timefromharvest,tocow,toreceptor, (units~sec)Thetransport timefrompasture,tocow,toreceptor, (units~sec)Allothertermsremainthesameasdefinedforthemilkpathway.TableC-2containsthevalueswhichwereusedincalculating g(M).Theconcentration oftritiuminmeatisbasedonairborneconcentration ratherthandeposition.

Therefore, theR~(M)isbasedonX/Q.RT(M)Where:K'KFPP~(DFL)~

[0~75(05/H))Q(M)~Dosefactorforthemeatingestion pathway.fortritiumforanyorganofinterest, (unitsmrem/yrperpCi/m')Allothertermsaredefinedabove.C.SVeetationPathwaTheintegrated concentration invegetation consumedbymanfollowstheexpression developed formilk.Manisconsidered toconsumetwotypesofvegetation (freshandstored)thatdifferonlyinthetimeperiodbetweenharvestandconsumption, therefore:

Q(V)~K'l,tbr(DFL)~U",Fe+U',F,eY(l,+A,).004152LL-83-Unit1ODCMRevision14June1994

APPENDIXC(Cont'd)Where:W(V)Dosefactorforvegetable pathwayforradionuclide ifortheorganofinterest, (units~m~-mrem/yr perpCi/sec)K'LU',FFAconstantofunitconversion, 1E6pCi/pCiTheconsumption rateoffreshleafyvegetation bythereceptorinagegroupa,(units=kg/yr)Theconsumption rateofstoredvegetation bythereceptorinagegroupa(units~kg/yr)Thefractionoftheannualintakeoffreshleafyvegetation grownlocallyThefractionoftheannualintakeofstoredvegetation grownlocallyTheaveragetimebetweenharvestofleafyvegetation anditsconsumption, (units~sec)YyTheaveragetimebetweenharvestofstoredvegetation anditsconsumption, (units=sec)Thevegetation arealPdensity,(units=kg/m~)Allotherfactorshavebeendefinedpreviously.

TableC-3presentstheappropriate parameter valuesandtheirsourceinRegulatory Guide1.109Revision1.Inlieuofsite-specific data,valuesforFandF~of,1.0and0.76'espectively, wereusedinthecalculation.

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

Therefore, theRz(V)isbasedonX/Q:Rp(V)~KK(Uft.+U'afc](DFL)~

0.75(0.5/H)

Where:+(V).dosefactorforthevegetable pathwayfo'rtritiumforanyorganofinterest, (units~mrem/yrperpCi/m~).Allothertermsaredefinedinpreceeding sections.

004152LL-84-Unit1ODQ4Revision14June1994 0

TABLEC-lParameters forGrass-(Cow orGoat)-Milk PathwaysParameter Q,(kg/day)(DFL)>(mrem/pCi)

F(pCi/liter perpCi/day)Y,(kg/mi)Y,(kg/m~)t(seconds) t,(seconds)

U~(liters/yr)

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

Eachradionuclide Eachstableelement2.00.77.78x10~(90days)1.73x10~(2days)330infant330child400teen310adultReference Re.Guide1.109Rev.1TableE-3TableE-3TableE-15TableE-15TablesE-lltoE-14TableE-1(cow)TableE-2(goat)TableE-15TableE-15TableE-15TableE-15TableE-5TableE-5TableE-5TableE-5004152LL-85-Unit1ODCMRevision14June1994

TABLEC-2Parameters fortheGrass-Cow-Meat Pathway~PaameteFf(pCi/KgperpCi/day)U(Kg/yr)(DFL)>(mrem/pCi)

Y~(kg/m~)Y,(kg/m~)tb(seconds) tf(seconds)Q(kg/day)Vaue1.0(radioiodines) 0.2(particulates)

Eachstableelement0infant41child65teen110adultEachradionuclide 0.72.07.78E6(90days)1;73E6(20days)50Reference e.Gude.109evTableE-15TableE-15TableE-1TableE-5TableE-5TableE-5TableE-5TablesE-11toE-14TableE-15TableE-15Table.E-15TableE-15TableE-3004152LL-86-Unit1ODCMRevision14June1994

TABLEC-3Parameters fortheVegetable PathwayParameter r(dimensionless)

(DFL)>(mrem/pCi)

U"),(kg/yr)-infant-child-teen-adultU'),(kg/yr)-infant-child-teen-adultt(seconds) t~(seconds)

Y(kg/m)Value1.,0(radioiodines) 0.2(particulates)

Eachradionuclide 026426405206305208.6E4(1day)5.18E6(60days)2.0Reference Re.Guide1.109Rev.1TableE-1TableE-1TablesE-11toE-14TableE-5TableE-5TableE-5TableE-5TableE-5TableE-5TableE-5TableE-5TableE-15TableE-15TableE-15004152LL-87-Unit1QX8Revision14June1994

APPENDIXDDIAGRAMSOFLIQUIDANDGASEOUSTREATMENT SYSTEMSANDMONITORING SYSTEMS004152LL-88-Uni.t1ODCMRevt.sion 14June1994 0P