ML18017A285

Annual Effluent & Waste Disposal Rept for Jan-Dec 1995. W/ 960329 Ltr

ML18017A285
Person / Time
Site:	Susquehanna
Issue date:	12/31/1995
From:	BYRAM R G PENNSYLVANIA POWER & LIGHT CO.
To:	NRC OFFICE OF INFORMATION RESOURCES MANAGEMENT (IRM)
References
NUDOCS 9604020111
Download: ML18017A285 (376)

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.CATEGORY 1.REGULATOROZNPOg+TION DISTRIBUTION ArSTEM(RIDE)ACCESSION NBR:9604020111 DOCWDATE:

95/12/31NOTARIZED:

NOFACIL:50-387 Susquehanna Steam'Electric Station,Unit1,Pennsylva 50-388Susquehanna SteamElectricStation,Unit2,Pennsylva AUTH.NAMEAUTHORAFFILIATION BYRAM,R.G.

Pennsylvania PowerGLightCo.RECIP.NAME RECIPIENT AFFILIATION DOCKETN0500038705000388

SUBJECT:

"AnnualEffluent6WasteDisposalReptforJan-Dec1995."W/960329ltr.DISTRIBUTION CODE:IE4SDCOPIESRECEIVED:LTR IENCLISIZE:TITLE:50.36a(a)(2)

Semiannual EffluentReleaseReportsNOTES:05000387ERECIPIENT IDCODE/NAME PD1-2LAPOSLUSNY,C COPIESRECIPIENT LTTRENCLIDCODE/NAME 22,='D1-2PD11COPIESLTTRENCL11INTERNAL:

ACRSNRR/DRPM/PERB/B RGN1FILE1111,11CENT-HR'1.

11RGN1DRSS/RPB22EXTERNAL:

LITCOAKERS,DNOTES:1111NRCPDR11DU~'OTETOALL"RIDS"RECIPIENTS:

PLEASEHELPUSTOREDUCEWASTE!CONTACTTHEDOCUMENTCONTROLDESK,ROOMOWFNSD-5(EXT.

415-2083)

TOELIMINATE.YOUR NAMEFROMDISTRIBUTION LISTSFORDOCUMENTS YOUDON'TNEEDlrTOTALNUMBEROFCOPIESREQUIRED:

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Pennsylvania Power8LightCompanyTwoNorthNinthStreet~Allentown, PA18101-1179

~810/774-5151 RobertG.ByramSeniorVicePresidenr-/Vnc/ear 610/774-7502 Fax:610/774-5019 MARp9t996U.S.NuclearRegulatory Commission Attn.:DocumentControlDeskMailStationP1-137Washington, D.C.20555SUSQUEHANNA STEAMELECTRICSTATIONANNUALEFFLUENTdhWASTEDISPOSALREPORTDocketNo.50-387and50-388Inaccordance with10CFR50.36a(a)(2) andtheSusquehanna SESUnit1and2Technical Specifications, attachedistheAnnualEffluent&WasteDisposalReportforSSESUnits1and2coveringtheperiodJanuary1tl1roughDecember31,1995.Verytrulyyours,R..ymAttachment copy:NRCRegionIMr.C.Poslusny, Jr.,NRCSr.ProjectManager-OWFNMs.M.Banerjee, NRCSr.ResidentInspector

-SSESVSOe02OX<i 95aasaPDRADQCK05000387l RPDR

+1.~iPkPOIh

@0ANNUALEFFLUENT8cWASTEDISPOSALREPORTFORJANUARY-DECEMBER1995Pennsylvania Power&LightCompanyTwoNorthNinthStreetAllentown, Pennsylvania 18101-1179

\March1996...9604020111 SUSQUEHANNA STEAMELECTRICSTATIONANNUALEFFLUENTANDWASTEDISPOSALREPORTREPORTPERIOD:01/01/95-12/31/95Preparedby:R.K.BarclayHealthPhysicist Reviewedby:B.H.CarsonHealthPhysicist Approvedby:K.E.ShankSupervisor

-Environmental Services-NuclearPennsylvania Power&LightCompanyTwoNorthNinthStreetAllentown, Pennsylvania 18101 TABLEOFCONTENTSSECTIONPAGE1.Introduction andSupplemental Information 2.EffluentandWasteDisposalData3.Meteorological DataandDispersion Estimates 4.DoseMeasurements andAssessments 1337685.ChangestotheOffsiteDoseCalculation ManualandtheSolidWasteProcessControlProgram776.ReportsofException totheSSESEffluentMonitoring Program7.Correction toDosesReportedinPreviousSemiannual orAnnualEffluentandWasteDisposalReport82848.EffluentfromAdditional Monitored ReleasePoints86AppendixA AppendixBRevisions toSSESODCMRevisions toSSESSolidWasteProcessControlProgram(NDAP-QA-0646) 0LISTOFFIGURESPAGEFigure1:SSESAirborneEffluentReleasePoints~Figure2:SSESWaterborne EffluentReleasePathwayFigure3:Susquehanna RiverMonthlyAverageFlowRatesFigure4:SSESMonthlyLiquidRadwasteDischarge TotalsFigure5:SSESWindRose:10-meterSensorsFigure6:SSESWindRose:60-meterSensorsFigure7:SSESPasquillStability ClassPrevalences Figure8:AreasWithintheSSESSiteBoundaryOpentoMembersofthePublic6222340414273 SECTION1INTRODUCTION ANDSUPPLEMENTAL INFORMATION INTRODUCTION TheSusquehanna SteamElectricStation(SSES)islocatedinSalemTownship, LuzerneCounty,Pennsylvania.

ItisonthewestbankoftheSusquehanna River,8kmnortheast ofBerwick.TheStationconsistsoftwoboilingwaterreactorgenerating units,eachwith1,050MWnetelectrical capacity.

Thereactorandgenerating unitsweresuppliedbyGeneralElectric, whiletheBechtelCorporation servedasarchitect-engineer andconstructor.

Construction oftheStationbeganintheearly1970s.FuelloadbeganinUnit1inJulyof1982.Initialcriticality wasachievedintheUnit1reactoronSeptember 10,1982.Thereactorreached100%powerforthefirsttimeonFebruary4,1983.Commercial opeiation ofUnit1wasdeclaredonJune8,1983.Initialcriticality ofUnit2occurredonMay8,1984.Unit2wasdeclaredcommercial onFebruary12,1985.Airborneeffluents arereleasedfromtheSusquehanna Stationviafiverooftopventsonthereactorbuilding(seeFigure1).Eachventiscontinuously monitored, andaprogramofperiodicsarripling andanalysisisconducted asspecified intheplantTechnical Specifications.

Allwaterborne effluents arereleasedinbatchmodeandaresampledandanalyzedpriortorelease.Waterborne effluents fromthesitearereleasedintothecoolingtowerblowdownlinefordilutionpriortoreleasetotheSusquehanna River(seeFigure2).Blowdownlineflowratesareatleast5,000gpmduringperiodsofliquidradwasterelease.Thedilutedeffluentisintroduced totheriverbywayofaperforated diffuserpipeplacedontheriverbed.Thediffuserservestorapidlyanduniformly mixthestationdischarge withthemainflowoftheriver.Thisreportpresentsasummaryofthequantities ofradioactive materials whichwerereleasedfromtheSusquehanna SteamElectricStationduringtheperiodfromJanuary1,1995toDecember31,1995.Inaddition, thisreportservesasamediumfornotifying theUSNuclearRegulatory Commission staffofchangestoPPRL'sOffsiteDoseCalculation Manual(ODCM)andSolidWasteProcessControlProgram(PCP)anddocumentation ofanyexceptions totheSSESeffluentmonitoring programwhichmustbereportedperTechnical Specifications 3.3.7.10and3.3.7.11.

Asectioncontaining corrections toapreviously reporteddoseisalsoincluded.

Airborneandwaterborne radioactive effluentreleasestotheenvironment duringthereportperiodweresampledandanalyzedinaccordance withtherequirements oftheTechnical Specifications.

Allradioactive effluentreleaseswerewithintheconcentration andreleaselimitsspecified intheRadiological EffluentTechnical Specifications (RETS).Calculations andtermsutilizedinthisreportarethoseoutlinedintheSSESOffsiteDoseCalculation Manual(ODCIVI).

Section1containssupplemental information pertaining toeffluents fromtheSusquehanna plant.Includedareregulatory limits(Table1),samplingandanalysismethods,andcharacterization ofthenumberanddurationofbatchandabnormalreleases, ifany.Section2containseffluentandwastedisposaldataforthereportperiod.Table2containsasummation ofallairbornereleases, groupedintotheradionuclide categories ofgases,particulates, iodines,andtritium.Averagereleaseratesarepresented andcomparedtotheapplicable limits.Table3presentstheactivitytotalsofspecificradionuclides inairborneeffluents.

Waterborne effluents aresummarized inTable4.Averagedilutedconcentrations arepresented andcomparedtotheapplicable limits.Table5presentsthereleasequantities ofspecificradionuclides inwaterborne effluents overthereportperiod.Figure3liststheSusquehanna Rivermonthlyaverageflowratesfor1995whileFigure4presentstheSSESmonthlyliquidradwastedischarge totalsfor1995.Tables6through17presentacharacterization ofthesolidradioactive wasteshippedoffsiteduringthereportperiod.Includedarethevolumesandcuriecontentsassociated witheachtypeofsolidwaste.Anestimateofmajornuclidecomposition ispresented foreachwastetype,aswellasthenumberofwasteshipments fromthesite,howtheyweretransported, andtheirfinaldestination:

Table18containsestimates oftheerrorsassociated withthemeasurements involvedinquantifying effluents.

Samplingerrors,countingerrors,anderrorsassociated withdetermining effluentflowratesandvolumesallcontribute tothetotalerrorofeffluentmeasurements.

Errorestimates arepresented foreachcategoryofradionuclide detectedinairborneandwaterborne effluents andsolid.wastesduringthereportperiod.Table19presentseffluentdatafrompreviousreportperiodswhichwas'notavailable atpreparation timefortheassociated annualreport.'ection3ofthisreportcontainsthemeteorological dataassociated withtheyear1995.Availability datafortheSSESmeteorological dataareshowninTable20.Meteorological dataforthecalendaryearispresented intheformofjointwindfrequency distributions byatmospheric stability class.Thesedistributions arepresented inTable21.Figures5and6arewindroseplotsfortheSSESprimarymeteorological 10-meterand60-metersensors,respectively.

Figure7presentstherelativeprevalences ofthePasquillstability classes.Inaddition, themeteorological datafromthereportyearwereusedtogenerateannualaveragerelativeconcentrations (X/Qs)anddeposition rates(D/Qs).Thesevaluesarepresented inTable22,andarerequiredinputforuseoftheGASPARcodeforcalculation ofthedosesresulting fromairbornereleases.

II0 Section1containssupplemental information pertaining toeffluents fromtheSusquehanna plant.Includedareregulatory limits(Table1)samlianalsismethoy'ds,andcharacterization ofthenumberanddurationofbatchandabnormalreleases, ifany.Section2containseNuentandwastedisposaldataforthereportperiod.Table2containsasummation ofallairbornereleases, groupedintotheradionuclide categories ogases,particulates, iodines,andtritium.Averagereleaseratesarepresented andcomparedtotheapplicable limits.Table3presentstheactivitytotalsofspecificradionuclides inairborneeffluents.

Waterborne eNuentsaresummarized inTable4.Averagedilutedconcentrations arepresented andcomparedtotheapplicable limits.Table5thFiure3listsiiesospeciicradionuclides inwaterborne effluents overthereport'.'g'heSusquehanna Rivermonthlyaverageflowratesfor1995whileepoperio.Figure4presentstheSSESmonthlyliquidradwastedischarge totalsfor1995.Tables6throuh17g.presentacharacterization ofthesolidradioactive wasteshippedoffsiteduringthereportperiod.Includedarethevolumesandcuriecontentsassociated witheachtypeofsolidwaste.Anestimateofmajornuclidecomposition ispresented foreachwastetype,aswellasthenumberofwasteshipments fromthesite,howtheyweretransported, andtheirfinaldestination Table18containsestimates oftheerrorsassociated withthemeasurements involvedinquantifying effluents.

Samplingerrors,countingerrors,anderrorsassociated withdetermining effluentflowratesandvolumesallcontribute tothetotalerrorofeNuent'measurements.

Errorestimates arepresented foreachcategoryofradionuclide detectedinairborneandwaterborne effluents andsolidwastesduringthereportperiod.avaiTable19presentseffluentdatafrompreviousreportperiodswhcht'lableatpreparation timefortheassociated annualreport.iwasnoSection3ofthisreportcontainsthemeteorological dataassociated w'thth.Availability datafortheSSESmeteorological dataareshowninTable20.ieyearMeteorological dataforthecalendaryearispresented intheformofjointwindfrequency distributions byatmospheric stability class.Thesedistributions arepresented inTable21.Figures5and6arewindroseplotsfortheSSESrimameteorolo ical10-meg'meterand60-metersensors,respectively.

Figure?presentstherelativeprevalences ofthePasquillstability classes.Inaddition, themeteorological datafromthereportyearwereusedtogenerateannualaveragerelativeconcentrations (XJQs)anddeposition rates(D/Qs).Thesevaluesarepresented inTable22,andarerequiredinputforuseoftheGASPARcodeforcalculation ofthedosesresulting fromairbornereleases.

Section4ofthisreportcontainsanassessment ofthecalculated dosesattributed tothereportedradiological effluents forthecalendaryear.TheLADTAPIIcodewasusedforcalculation ofdosesfromwaterborne effluents.

Table23containssite-specific parameters usedforLADTAPIIcalculations, fortheDanvillereceiver.

TheGASPARcodewasusedforcalculation ofdosesfromairborneeffluents.

Thecalculated dosesanddirectradiation estimates canbeusedtoestimatethedosestomaximally exposedmembersofthepublic.Table24summarizes maximumcalculated dosesanddosecommitments tomembersofthepublicfromairborneandwaterborne effluents anddirectradiation.

Table25presentscalculated collective dosestomembersofthepublicwithintheRiverlands/Information CenterComplex.Table26summarizes thecalculated dosesforresidences andotheroccupiedareaswithintheSSESsiteboundary.

Table27reportsdosescalculated forthenearestdairyfacility.

Section5ofthisreportisreservedfordocumentation ofchangestotheOffsiteDoseCalculation ManualandtheSolidWasteProcessControlProgram.AcopyofchangestotheODCMduringthereportperiodisincludedinAppendixA.AcopyofchangestotheSolidWasteProcessControlProgramisincludedinAppendixB.Section6presentsalistingofcases(ifany)inwhichairborneorwaterborne effluentmonitoring instrumentation wasdeclaredinoperable andwasnotrestoredtooperability withinthetimeperiodspecified inTechnical Specification Table3.3.7.10-1 or3.3.7.11-1 ActionStatements.

Section7containscorrections todosesreportedinpreviousSemi-annual orAnnualEffluentandWasteDisposalreports.(Table28)Section8containsinformation oneffluent(Table29)andoffsitedose(Table30)fromadditional monitored releasepoints.

FIGURE1SSESAIRBORNEEFFLUENTRELEASEPOINTSUNITIhEACTOhWILOINOEXHAUSTVKHTISLESCfMATOl+F110'THhEACTDhWILDIHOEXHAUSTVENTIlLKOCfM,ATNFIl04f220AXXICfM1240CfM2QSXOCfMAT100+I120ffAT120~fAT100+K12IWFOUTSIDEAlhINTAKEHEACTOh4UILOIHQEXHAUSTSTACKSDIESELEXHAUSTFLENUMDIESELOEHEHATOhWILDHID~%~~%EL.4)a'I "UNITITUXEIHE0UILOINCEXHAUSTVENTUNITIITUXSHIESUILOHIOEXHAUSTVENTlbhADW4WILDINGL4IrrIISo+24-+rr 21'~TUhEINESUILOINOJgUNITIEL414'4UNITII It rIlFIGURE2SSESWATERBORNE EFFLUENTPATHWAYIIIl~~~I,IatguyZ~a~uXg)i)anoaePQIIcC~Ig4gIeee~gP,Qn~egre(4I~n<>oII~IIv5cXnnIeldOOOCIIIeJI

SUPPLEMENTAL.lNFORMATlON 1.ReulatoLimitsTechnical Specifications 3/4.11.1and3/4.11.2outlinerequirements forreleaseofradioactive liquidandgaseouseffluents, respectively.

Concentration ofradioactive materials releasedinliquideffluents anddoseordosecommitment resultant thereofarelimitedinunrestricted areas.Doseanddoserateduetoradioactive materials releasedingaseouseffluents arelimitedinareasatorbeyondthesiteboundary.

Technical Specification limitsarelistedinTable1.2.MaximumPermissible Concentrations inWaterborne Effluents Theconcentrations ofradioactive materials inwaterborne effluents arelimitedtotheconcentrations specified in10CFRPart20AppendixBTableII,Column2,forradionuclides otherthandissolved orentrained noblegases.Fordissolved orentrained noblegases,theconcentrations arelimitedtothefollowing values,asstatedintheapplicable Technical Specification:

NuclideMPCuCi/ml85mK85K87K88K"'AI133mX133X135mx135X2.0E-045.0E-044.0E-059.0E-057.0E-055.0E-046.0E-042.0E-042.0E-043.A~~Basedongaseouseffluentreleasesforthereportperiodaveragebetaenergyis,0.319MeVandaveragegammaenergyis0.249MeV.4.Measurements andAroximations ofTotalRadioactivi Analysesofspecificradionuclides ineffluentsamplesareusedtoevaluatetheradioactive composition andconcentration ofeffluents.

5.MethodsofuantifinEffluents

'issionandActivation Gases:Gassamplesareroutinely collected monthlyandanalyzedwithahighresolution (Ge[Li]orHPGE)detectorsystemwhichincoroorates adatareduction programtodetermine radionuclide composition intermsofspecificactivity.

Datatapesfromthecontinuous ventmonitorsareusedtodetermine theaverageconcentration ofnoblegases:Thehighresolution (Ge[Li]orHPGE)isotopicscanisusedtoconvertthecontinuous'vent monitoractivitytoactualactivitybasedonthedetermined nuclidemixture.Theventandsampleflowratesarecontinuously monitored, andtheaverageflowratesforeachventareusedtocalculate thetotalactivityreleasedinagiventimeperiod.Whenthecontinuous monitorsareoutofservice,manualgrabsamplesaretakenfromeachventonceeacheighthours(onceeachfourhoursforthestandbygastreatment vent).b.C.lodines:iodineiscontinuously collected viaanisokinetic samplingassemblyineachvent.Filtersarenormallyexchanged onceperweekandanalyzedonahighresolution (Ge[Li]orHPGE)system.Thedailyaverageflowratesfortheventsandsamplepumpsareaveragedforthedurationofthesa'mpling period,andaratioofventflowratetosampleflowrateisdetermined.

Theratioisusedtodetermine thetotalactivityofeachisotopereleasedduringthetimeperiodinquestion.

Whenthecontinuous monitorsareoutofservice,iodineiscontinuously collected oncharcoalcartridges attachedtoairsamplerswhichdrawdirectlyfromtheaffectedrooftopvent(s)orfromalternate samplingportsavailable onthesamplelines.'IParticulates:

Particulates arecontinuously collected viaanisokinetic samplingassemblyineachvent.Filtersarenormallyexchanged onceperweekandanalyzedonahighresolution (Ge[Li]orHPGE)system.Flowratecorrections areperformed asforiodines.Whenthecontinuous ventmonitorsareoutofservice,particulates arecontinuously sampleddirectlyfromtheaffectedrooftopvent(s)orfromalternate samplingportsavailable onthesamplelines.Tritium:Airbornetritiumiscollected monthlyviabubblersampler.Thesampleiscollected foronehourataflowrateofapproximately 1000cclmin.Tritiumactivityinthebubblersampleisdetermined byliquidscintillation counting.

Theliquidsampletritiumconcentration isconverted toairconcentration byvolumeproportion, thencomparedtotheTechnical Specification Table4.11.2.1.2-1 LowerLimitofDetection (1E-6uCi/cc).

j<

IWaterborne Effluents:

Eachtankofliquidradwasteissampledandanalyzedforprincipal gammaemitterspriortorelease.Eachsampletankisrecirculated forasufficient amountoftimepriortosamplingtoensurethatarepresentative sampleisobtained.

Samplesareanalyzedonahighresolution (Ge[Li]orHPGE)systemandreleasepermitsaregenerated basedonthevaluesobtainedfromtheisotopicanalysisandthemostrecentvaluesfortritium,grossalpha,iron-55,andstrontium-89 and-90.Analiquotbasedonreleasevolumeissavedandaddedtomonthlyandquarterly composite containers.

Themonthlytritiumanalysisisdonein-house.

Thequarterly composite issenttoavendorlaboratory foriron-55,strontium-89 and-90,andgrossalphaanalyses.

Theconcentration ofeachradionuclide ineachbatchisdecaycorrected fromthetimeofcountingtothemidpointofthereleaseperiod,andisthenmultiplied bythevolumeofthebatchtodetermine thetotalquantityofeachnuclidereleasedineachbatch..Theisotopictotalsforeacharesummedtodetermine thetotalsourcetermforthereportperiod.

TABLE11.TECHNICAL SPECIFICATION LIMITSA.NOBLEGASES:1.s500mrem-TOTALBODY<3000mrem-SKIN"-annualsitetotal"instantaneous" limits(TechSpec.3.11.2.1) 2.<5mrad-AIRGAMMAs10mrad-AIRBETAquarterly airdoselimitsperreactorunit(TechSpec.3.11.2.2) 3.c10mrad-AIRGAMMA&<0mrad-AIRBETAannualairdoselimitsperreactorunit(TechSpec.3.11.2.2)

B.AIRBORNEI-131,TRITIUM,PARTICULATES WITHHALF-LIVES

>8DAYS:s1500mrem-ORGAN'inhalation pathwaysonly)annualsitetotal"instantaneous" limits(TechSpec.3.11.2.1)

'-2.s7.5mrem-'ORGANquarterly doselimitsperreactorunit(TechSpec.3.11.2.3) 3.c15mrem-ORGANannualdoselimitsperreactorunit(TechSpec.3.11.2.3) 10 C.~LIUIOEFFLUEMTR 1.Concentration g10CFR20AppendixB,TableII,Column2-sitetotal"instantaneous" limits(TechSpec.3.11~1.1)s5mrem-ORGANquarterly doselimitsperreactorunit(TechSpec.3.11.1.2) t3.s3mrem-TOTALBODYs10mrem-ORGANannualdoselimitsperreactorunit(Tech.Spec.3.11.1.2)

D.AIRBORNEEFFLUENT:

BASESFORPERCENTOFAPPLICABLE TECHNICAL SPECIFICATION LIMITFissionandActivation GasesAderivedreleaseratelimitbasedontheTechnical Specification limitof500mrem/yrwascalculated fromtheexpectedmixofnoblegasradionuclides

'resented inTable4.4oftheSSESFinalEnvironmental Statement (NUREG-0564).

Thelimitis8.51E+05uCi/min(1.42E+04 uCi/sec).

Iodine-131AderivedreleaseratelimitbasedontheTechnical Specification limitof1500mrem/yrfroml-131,tritiumandparticulates withhalf-lives greaterthan8dayswascalculated fromtheannualreleasequantityofI-131providedinTable44oftheSSESFinalEnvironmental Statement (NUREG-0564).

Thelimitis1.41E+02uCi/min(2.35E+00 uCi/sec).

Particulates Aderivedreleaseratelimit.basedontheTechnical Specification limitof1500mrem/yrfroml-131,tritiumandparticulates withhalf-lives greaterthan8dayswascalculated basedontheexpectedmixofparticulate radionuclides presented inTable4.4oftheSSESFinalEnvironmental Statement (NUREG-0564).

Thelimitis7.72E+02uCi/min(1.29E+01 UCI/sec).11 TritiumAderivedreleaseratewascalculated basedonthe10CFR20AppendixB,TableII,Column1,MaximumPermissible Concentration fortritium(2.0E-07uCi/cc)tounrestricted areas.Arelativeconcentration of4.1E-05sec/m'wasassumed.Thelimitis2.93E+05uCi/min(4.88E+03 uCi/sec).

F.WATERBORNE EFFLUENT:

BASESFORPERCENTOFAPPLICABLE TECHNICAL SPECIFICATION LIMITFissionandActivation ProductsConcentrations offissionandactivation productsinliquideffluentfromradwasteeffluentaredetermined foreachbatchpriortorelease.Eachisotopeconcentration iscomparedto10CFR20AppendixB,TableII,Column2MaximumPermissible Concentration Limitssuchthat,withdillution, thesumofisotopeconcentrations dividedbyMaximumPermissible Concentrations mustbe<1.0.NoTechnical Specification limitforthetotalconcentration offissionandactivation productsinliquideffluents isapplicable forthiscategory.

TritiumLiquideffluentquarterly tritiumconcentrations arecomparedtothe10CFR20AppendixB,TableII,Column2,MaximumPermissible Concentration limitof3.0E-03uCi/mltounrestricted areas.Dissolved andEntrained GasesLiquideffluentquarterly concentration totalsfordissolved andentrained gasesarecomparedtothemostrestrictive MaximumPermissible Concentration foranoblegas4.0E-05uCi/ml(Kr-87)fromtheSSESTechnical Specification Table3.11.1.1-1.

12 SECTION2EFFLUENTANDWASTEDISPOSALDATA13

AirborneEffluents Summaries oftheradionuclide totalcurieactivities andaveragereleaseratesareincludedinTables2and3.ThirdFourthQuarterQuarter~1.NumberofBatchReleases:

.2.TotalTimePeriodforBatchRelease:3.MaximumTimePeriodforaBatchRelease:4.AverageTimePeriodforaBatchRelease:5.MinimumTimePeriodforaBatchRelease:0NANANA'A0NANANANAAbnormalReleases1.NumberofReleases2.TotalActivityReleased0NA0NAIfaradionuclide wasnotdetected, zeroactivitywasusedforthatisotopeindosecalculations.

Azeroactivityindicates thatnoactivitywaspositively detectedinanysamplewhensampleswereanalyzedwithtechniques whichachievedtherequiredLowerLimitsofDetection (LLD)asspecified intheSSESTechnical Specification Table4.11.2.1.2-1, Radioactive GaseousWasteSamplingandAnalysisProgram.Inallcases,theseLLDswerelessthanthelevelsrequiredbyTechnical Specifications.

Thefollowing aretypicalLLDs.Radionuclide LLD(uCI/cc)Kr-87Kr-88Xe-133Xe-133mXe-135Xe-135mXe-1384.6E-085.3E-085.4E-081.3E-071.5E-085.0E-081.2E-07Mn-54Fe-59Co-58Co-60'n-65Mo-99Cs-1342.9E-142.8E-141.8E-143.8E-144.4E-143.3E-132.4E-1414 Radionuclide Cs-137Ce-141Ce-144l-131Sr-89Sr-90H-3GrossAlphaLLD(uCi/cc)2.1E-141.5E-147.0E-144.4E-142.0E-153.0E-162.6E-085.0E-1615

TABLE2ANNUALEFFLUENTANDWASTEDISPOSALREPORT(1995)AIRBORNEEFFLUENT-SUMMATION OFALLRELEASESA.FissionandActivation GasUnitFirstuarterSeconduarterThirduarterFourthuarterTotalReleaseCi'.32E-02 1.53E+010.00E+00O.OOE+00AverageReleaseRateforPeriodPercentofTechnical Specification Limit5.76E-051.38E-02uCi/sec8.13E-031.95E+00O.OOE+000.00E+000.00E+00O.OOE+00B.IodinesTotalI-131AverageReleaseRateforPeriodCi0.00E+000.00E+00uCi/scc0.00E+000.00E+000.00E+000.00E+000.00E+00O.OOE+00PercentofTechnical Specification LimitQ.OOE+000.00E+000.00E+00O.OOE+00C.Particulate

~~Particulate withHalf-Lives

>8Days*Ci2.18E-044.60E-047.33E-059.35E-04AverageReleaseRateforPeriodPercentofTechnical Specification LimitGrossAlphaRadioactivity*

uCi/secCi2.80E-05'2.17E-04 1.06E-065.85E-054.55E-042.85E-079.22E-067.18E-05'.18E-049.15E-040.00E+00O.OOE+00D.TritiumTotalReleaseAverageReleaseRateforPeriodCiuCi/sec1.59E+012.04E+001.24E+011.58E+002.36E+011.02E+012.97E+001.28E+00PercentofTechnical Specification Limit4.17E-023.22E-026.06EA22.62E-02*Sr-89,Sr-90andGrossAlphavaluesforthefourthquarter1995areestimated basedonthirdquarter1995sampleanalysesandfourthquarter1995ventilation exhaustrates.16

TABLE3ANNUALEFFLUENTANDWASTEDISPOSALREPORT(1995)AIRBORNEEFFLUENTReleasesinContinuous ModeNuclidesReleasedA.FissionandActivation GasesUnitFirstQuarterSecondQuarterThirdQuarterFourthQuarterKr-85mXe-133Xe-135TotalforPeriodB.IodinesI-131I-133I-135TotalforPeriodC.Particulate Cr-51Mn-54Fe-59Co-58Co-60Zn-65Sr-89~Sr-90*Cs-134Cs-137Ce-141Ce-144TotalforPeriod~CiCiCiCiCiCiCiCiCiCiCiCi,CiCiCiCiCiCiCiCiCiCiCi0.00E+000.00E+000.00E+006.32E-.02 6.32E-02O.OOE+000.00E+000.00E+000.00E+001.62E-051.10E-040.00E+002.51E-052.99E-053.65E-050.00E+001.26E-070.00E+000.00E+000.00E+000.00E+002.18E-040.00E+000.00E+00'.00E+00 1.53E+011.53E+010.00E+00O.OOE+000.00E+000.00E+002.46E-053.43E-044.54E-050.00E+004.70E-05O.OOE+000.00E+000.00E+000.00E+000.00E+000.00E+000.00E+004.60E-040.00E+000.00E+00O.OOE+00O.OOE+00O.OOE+00O.OOE+00O.OOE+00O.OOE+00O.OOE+000.00E+000.00E+000.00E+000.00E+001.71E-05O.OOE+00O.OOE+000.00E+001.71E-050.00E+000.00E+004.95E-056.41E-040.00E+001.58E-040.00E+000.00E+002.38E-051.36E-040.00E+000.00E+000.00E+00'.OOE+00 O.OOE+00O.OOE+00O.OOE+00O.OOE+000.00E+000.00E+00O.OOE+00O.OOE+000.00E+000.00E+007.33E-059.35E-04*Reported valuesforthefourthquarter1995areestimated basedonthirdquarter1994sampleanalysesandfourthquarter1995ventilation exhaustrates.

Waterborne ENuentsSummaries oftheradionuclide totalcurieactivities, averagedilutedconcentrations, andpercentofapplicable Technical Specification limitsareincludedinTables4and5.BatchReleases"

'.NumberofBatchReleases2.TotalTimePeriodforaBatchRelease3.MaximumTimePeriodforaBatchRelease4..AverageTimePeriodforaBatchRelease5.MinimumTimePeriodforaBatchRelease6.AverageStreamFlowDuringPeriodofReleaseofEffluentintoaFlowingStreamQtr.1gtr.2gtr.34070525.11E+031.30E+045.07E+033.08E+025.64E+023.48E+02gtr.4621.10E+045.20E+021.28E+021.86E+029.75E+012.50E+01.1.00E+00 2.00E+011.78E+022.40E+Ol(CoolingTowerBlowdownFlowRate)6.76E+036.86E+031.00E+047.60E+037.94E+063.95E+066.53E+055.94E+06(Susquehanna RiverFlowRate)<<Unitsoftimeandflowareexpressed inminutesandgallonsperminute(gpm),respectively.

AbnormalReleases1.NumberofReleases2.VolumeReleased3.TotalActivityReleased0N/AN/A0N/AN/AIfaradionuclide wasnotdetected, zeroactivitywasusedforthatisotopeindosecalculations.

Azeroactivityindicates thatnoactivitywaspositively detectedinanysamplewhensampleswereanalyzedwithtechniques whichachievedtherequiredLowerLimitsofDetection (LLD)asspecified intheSSESTechnical Specification Table4.11.1.1.1-1, Radioactive LiquidWasteSamplingandAnalysisProgram.Inallcases,theseLLDswerelessthanthelevelsrequiredbyTechnical Specifications.

Thefollowing aretypicalLLDs.Radionuclide LLDuCi/mlMn-54Fe-59Co-58Co-60Zn-65Mo-99I-131Cs-1344.5E-085.0E-082.4E-085.4E-084.9E-081.7E-072.0E-082.2E-0818

Radionuclide LLDuCi/mlCs-137Ce-141Ce-144Sr-89Sr-90Fe-55H-3GrossAlpha2.6E-083.2E-081.3E-074.0E-084.0E-091.0E-064.6E-063.0E-0819 TABLE4ANNUALEFFLUENTANDWASTEDISPOSALREPORT(1995)WATERBORNE EFLUENT-SUMMATION OFALLRELEASESA.FissionandActivation ProductsUnitFirstQuarterSecondQuarterThirdQuarterFourthQuarter'1.TotalRelease(notincluding Tritium,Gases,AIh'a~2.AverageDilutedConcentration DuringPeriod3.PercentofA licableLimit CiuCi/ml5.91E-024.44E-013.43E-024.52E-071.27E-061.81E-07O.OOE+00'.OOE+00O.OOE+004.21E-021.37E-070.00E+00B.Tritium1.TotalReleaseCi1.68E+012.75E+019.32E+002.57E+012.AverageDilutedConcentration DuringPeriod3.PercentofAlicableLimituCi/ml1.28E-044.28E+007.86E-052.62E+004.91E-051.64E+008.37E-052.79E+00C.Dissolved andEntrained GasesTotalReleaseAverageDilutedConcentration DuringPeriodCiuCi/ml1.51E-041.15E-093.34E-033.19E-059.54E-091.68E-105.45E-041.77E-093.PercentofAlicableLimitD.GrossAlhaRadioactivi 1.TotalReleaseCi2.88E-052.39E-044.20E-064.43E-.05 0.00E+000.00E+000.00E+000.00E+00E.VolumeofWasteReleased(PriortoDilution)

Gallons3.95E+053.07E+063.08E+058.25E+05Liters1.50E+061.16E+071.17E+063.13E+06F.VolumeofDilutionWaterUsedDuringPeriodofReleaseGallons3.45E+079.22E+075.01E+078.10E+07Liters1.31E+083.50E+081.90E+083.07E+08G.VolumeofDilutionWaterUsedOverEntirePeriodGallons8.76E+088.99E+081.32E+091.01E+09Liters3.39E+093.48E+095.13E+093.90E+09~Reported valuesforthefourthquarter1995areestimated basedonthirdquarter1995sampleanalysesandfourthquarter1995discharge volumes.20 TABLE5ANNUALEFFLUENTANDWASTEDISPOSALREPORT(1995)WATERBORNE EFFLUENTNuclldesReleasedUnitReleasesinBatchModeFirstQuarterSecondQuarterThirdQuarterFourthQuarterA.FissionandActivation ProductsF-18Na-24Cr-51Mn-54Mn-56Fe-55Fe-59Co-58As-76Sr-89Sr-90Sr-92Nb-95Tc-99mA-110mSb-124Te-131m1-131Cs-134Cs-137La-140Cc-144Hi'-181W-187TotalforPeriod'.TritiumH-3.TotalforPeriodCiCiCiCiCiCiCiCiCiCiCiCiCiCiCiCiCiCiCiCiCiCiCiCiCiCiCiCiCi0.00E+002.21E454.64E425.56E43O.OOE+002.69E432.05E431.40E441.74E432.20E441.89E440.00E+00O.OOE+004.24E480.00E~3.05E463.49E45O.OOE+000.00E+000.00E+002.79E462.72E45O.OOE+00O.OOE+000.00E+000.00E+005.91E421.68E+Ol1.68E+Ol3.94E-13O.OOE+001.85E428.66E420.00E+002.72E413.63E425.17E431.93E423.72E430.00E+00O.OOE+00O.OOE+M6.53E463.15E466.89E471.94E435.28E444.01E45O.OOE+002.88E463.46E45O.OOE+001.08E445.03E45O.OOE+004.44E412.75E+012.75E+010.00E+M7.42E445.60E452.57E422.24E-IO5.47E431.94E441.51E441.45E434.50E440.00E+000.00E+000.00E+005.48E474.71E463.58E479.43E45O.OOE+00O.OOE+00O.OOE+001.13E462.15E45O.OOE+00O.ME+000.00E+000.00E+M3.43E429.32E+009.32E+000.00E~O.OOE+003.49E432.07E42O.OOE+005.47E436.13E436.86E443.91E435.86E44O.OOE40O.OOE+000.00E+005.71E460.00E+000.00E401.10E433.21E450:OOE+00O.OOE+004.22E461.17E458.23E46O.OOE+00O.OOE+00O.OOE+004.21E422.57E+012.57E+OlC.Dissolved andEntrained GassesKr-86mKr-85Kr-87Kr-88Xe-131mXc-133mXc-133Xe-135mXc-135TotalforPeriodCiCiCiCiCiCiCiCiCiCiCi0.00E+00O.OOE+00O.OOE+000.00E+000.00E+00O.OOE+000.00E+003.66E-OSO.OOE+001.14E441.5IE44O.OOE+M0.00E+003.07E43O.OOE+00O.OOE+00O.OOE+00O.OOE+001.75E440.00E+009.15E453.34E43O.OOE+000.00E+000.00E+00O.OOE+00O.OOE+000.00E+000.00E+001.65E45O.OOOO1.54E453.19E45O.OOE+00O.OOE+003.86E440.00E+00O.OOE+000.00E+00O.OOEt009.05E45O.OOE+006.83E455.45E44<<Reported valuesforthefourthquarterareestimated basedonthirdquarter1995sampleanalysesandfourthquarter1995discharge volumes.

FIGURE3SUSQUEHANNA RIVERMONTHLYAVERAGEFLOWRATESDATAPERIOD:1995GALLONSPERMINUTEx1E612-.:*8:--'=-".':::::::,:::

'-"...'::.":.*642-.0JFMAMJJAS0ND199522 FIGURE4SSESMONTHLYLIQUIDRADWASTEDISCHARGE TOTALSDATAPERIOD:1995GALLONSX1E3500,:.:...

400::::::::

300200'00'I'~,~i~,~0JFMAMJJAS0ND199523

SUSQUEHANNA STEAMELECTRICSTATIONRADIOACTIVE WASTEREPORTANNUALEFFLUENTANDWASTEDISPOSALREPORTSOLIDRADIOACTIVE WASTEDATAPERIOD:

JANUARY11995-DEEMBER311995PREPAREDBY:.P.LEWI-ALYSICISTAPPROVEDBY:E3SDOXSEY-LUENTSMANAGEMENT SUPV.24 REPORTNOTES1.Allactivities reportedinmillicuries (mCi)unlessotherwise noted.t2.Reportedactivities, asindicated withthe(<)sign,arecomprised inwholeorpartofMDLValues.3.NoClassCWastewasdisposedduringthisreportperiod.4.Thenumberofshipments listedinTable6includesonlytheshipments fromSSEStothedisposalsite.Itdoesnotincludeshipments madetoorfromvolumereduction vendors.25 TABLE6ANNUALEFFLUENTANDWASTEDISPOSALREPORTSOLIDWASTEANDIRRADIATED FUELSHIPMENTS DATAPERIOD:JANUARY1,1995-DECEMBER31,1995A.*SOLIDWASTESHIPPEDOFFSITEFORBURIALORDISPOSALNumberofShimentsModeofTransortationDestination TruckBarnwell, SCB.IRRADIATED FUELSHIPMENTS NumberofShimentsModeofTransortationDestination NoneNotApplicable NotApplicable Thenumberofshipments listedinAincludeonlytheshipments fromSSEStoadisposalsite.Itdoesnotincludeshipments madetoorfromvolumereduction vendors.26 TABLE11CLASSASOURCEOFWASTEINCINERATED DAWTYPEOFCONTAINER STRONGTIGHTCONTAINER METHODOFPROCESSN/AISOTOPES%OFTOTALAg-IlornAm-241C-14Cm-242Co-58~0Cr-51Cs-137Fc-55Fe-59H-31-129I-131Mn-54Ni<3Pu-238Pu-239Pu-241Sr-90Tc-99Zn<5I3c47Cm-244Cc-144KAO.Nb-95Pb-212Zr-95Xe-133TOTALACTIVITY(Ci)CONTAINER VOLUME(1.000EC4Q3.076'.621E+00 1.644EA32.596E+00 2.556E+02 1.501E426.911E+00 7.82&E+01 5.373E+0Iwnt&Ewl1.&OOE+32.280E%2.7.099E+02 1.627E+00 45.039E%4<6.063E~3.386EAl'1.004E%2 4.951E%21.859E+01 2.000E<a<3.985E%4~'.98&E+00 1.900E-03

'.150E-Oll.600E432.079E+00 1.200E<3I.174295.GOOA30.00%0.00%0.14%000%0.22%,2178%0.00%0.59/o6.67%458%4+o~0.00%0.00%60.48%0.14%0.00%P00%003%0nn/0l58%0.00io0.00%P17%P00%PP2%ppp0.l8%O.OO%100.00%8.37lm327 TABLE12CLASSASOURCEOFWASTEPROCESSED DAWTYPEOFCONTAINER STRONGTIGHTCONTAINER METHODOFPROCESSN/AISOTOPES%OFTOTALAm-241C-14Cm-242Co-58Co%0Cr-51Cs-137Fc-55Fc-59H-3I-l29'n-54Ni43Pu-238Pu-239Pu-241Sr-90Tc-99Zn<5Cm-243Cc-l44Nb-95Zr-95TOTALACTIVITY(Ci)CONTAINER VOLUME1.484EA34.336&015.992E+31.716'2.031E+02 4.728EO25.687E+00 6.313E&13.394E+01 1.321E+01 2.400E43.4.894E&2 1.321E+00 1237E<3,1.2718432.325EAI4.431E425.930E%2l.279E+0l6.832'.881E+00 L091E~6.933E+00~0.8351113.100fQP00%0.05%P00%0.21%24.32%'01%0.68'.56%

4.06%1.58%0.00%58.61%0.16%0.00%Q.00%003%Q.Q1%0.01%153%0.00%0.22%013%083%100Opoj31.520m31-129VALUESFORSOMECONTAINERS WERELISTEDWITHLLDVALUESOP3.01M4uCi/ccORLESSANDARENOTINCLUDEDINTHEABOVEI-129ACTIVITY.

28 F

TABLE13CLASSASOURCEOFWASTENON-PROCESSED DAWTYPEOFCONTAINER STRONGTIGHTCONTAINER METHODOFPROCESSN/AISOTOPESACTIVITY%OFTOTALAg-IipmAm-241C-14Cm-242Co-58GripCr-51Cs-137Fe-55Fe-59H-31-129Mn-54.Ni<3Pu-238Pu-239Pu-241Sr-90Tc-99Zn45Ce-144Cm-243TOTALACTIVITY(Ci)CONTAINER VOLUME1.180E<30.45%7.340EA70.00%2.700E4~0.08%4.370EW60.00%1.550EA30.59/o1.290'5000%5.250EA32.02'/03.500EA3I34%~4.060E+21573%2.780EA21077%7,62nE3"94oioN/ALLD(4.27E48uCi/cc)3.290E<21273%8.090E40.31/o5.660E70.00%6.110EW7000%1.450E40.05o/o1.360E50.00%1440E<5001/6.440EW32.48%1.270E<3050/o3.660EW70.00%0.00010000%5.9II0.167m329 TABLE14CLASSBSOURCEOFWASTERWCUFILTERMEDIATYPEOFCONTAINER HICMETHODOFPROCESSDEWATERED ISOTOPESACTIVI'IY

%OFTOTALAm-241C-14Cm-242GHM,Cs-137Fe-55H-3I-129Mn-54Ni<3Pu-238Pu-239Pu-241SR49Sr-90Tc-99Zn<5Ce-144Ni-59Cm-243TOTALACTIVITY(Ci)CONTAINER VOLUME7.810E42"PPP%6.250E+00 9.00%5.160E420.00%5.210E+05 48.56%1.619E+03 0.15%'.230E+05 2078%2A60E410.00%N/ALLD(1.45E46uCi/cc)2.870EW52675%8.170E&30.76%1.942E42.PPP%1.956E420.00%1.93&E+01 0.00'/o7.490E410.00%2.240Et00 000/9.370'001%3.030E~2.82%9.750E+00 0.00%1.640E+03 017%7.660E<20.00%1073.000100.00%264.800.ft7.498m330 TABL'E15CLASSASOURCEOFWASTECONDENSATE DEMINERALIZER RADWASTEDEMINERALIZER TYPEOFCONTAINER HICMETHODOFPROCESSDEWATERED ISOTOPESACTIVITY%OFTOTALAm-241C-14Cm-242Co-58GripCs-137Fe-55Fe-59H-31-129Mn-54Ni43Pu-238Pu-239Pu-241Sr-90Tc-99'n45Ce-144Cm-243TOTALACTIVITY(Ci)CONTAINER VOLUME1.756E435.263E&01.756E436.442E+01 5.033'3.894E412.234E+00 3.150E411.448E+01 N/ALLD(2;85E452.132E+01

.8.897E412.335E432.425E435.571E411.081E42N/ALLD(4.57E451.853E&05.362E411.572E430.16387.600fl0.00%324%PPP%39.61%30.94%0.24%137%0.19%8.90%uCi/cc)13.11%055%P00%0.00%0.35%PP1%uCi/cc)115%034%0.00/o1PPPP%2.481m3

TABLE16CLASSASOURCEOFWASTEULTRASONIC RESINCLEANINGWASTETYPEOFCONTAINER HICMETHODOFPROCESSDEWATERED ISOTOPESACTIVITY%OFTOTALAg-IlornAm-241C-14Cm-242Co-58~0Cr-51Cs-137Fc-55Fe-59H-31-129Mn-54Ni<3Pu-238Pu-239Pu-241Sb-124Sr-90Tc-99Zn45Cc>>144Cm-243Ni-59TOTALACTIVITY(Ct)CONTAINER VOLUME1.664E+020.41%8.600E<3Q00'/5.200E+01

'13%5.600E%3P00%2.863E&2071%6.200E&315.24%3.700E+02 091%2.220E+01 0.06%6.260E+03 15.38%1.795E+03 442%5.680E+01 014%N/ALLD(6.53E45uCi/cc)2.490E+04 61.18%1.078E+02027%1.824E%2P00%1.69IE42,0.00%4.130E+00 001%,4.680E+01 0.12%2.340EAI000%2.720E%1Q.uu%4060E+02'00/1.110E+0(}u(l(kvio5.610E%3Q.oo%6.7IQE+00002%40.70010000'I362.700ft10.271m332 TABLE17CLASSASOURCEOFWASTELIQUIDRADWASTEFILTERMEDIATYPEOFCONTAINER HICMETHODOFPROCESSDEWATERED ISOTOPESACTIVITY%OFTOTALAg-IlpmAm-241C-14Cm-242Co-58Co%0Cr-SlCs-137Fe-55Fe-59H-31-129Mn-54Ni<3Pu-238Pu-239Pu-241Sb-124Sr-89Sr-90Tc-99*Zn45Ce-144Cm-243Hf-181Nb-95Ni-59Sr-92TOTALACTIVITY(Ci)CONTAINER VOLUME3.223E&22.560'2.377E+00 2.509EI2'.959E+03 2.783E&48.496E+03 7.416EWI2.406E+04 1.173E+04 1.213E+02 N/ALLD1.006E&53.576E+02 5.433'5.032'1.227E+02 2.678E+02 4.336E+00 9.318E&11.080E+003.520E+03 1.248E+02

.'.257EAI 2.631E+01 7.619E+01 9.576E+0I7.910E-16 180.790777.600018%0.00%PPP%0.00%64%IS39%470%0.04%13.31%649%007%(4.75E45uC1/cc)55.64%0.20%PPP%PP0%0.07%0.15%0.00%U.UU"jo0.00%l.950jo0.07%PPP%PP1%pp40.05%PPP%10000j'22.020n13TC-99VALUESFORSOMECONTAINERS WERELISTEDWITHLLDVALUESOF8.84c-pSuCi/ccORLESSANDARENOTINCLUDEDINTHEABOVETC-99ACTIVITY.

33 TABLE18ANNUALEFFLUENTANDWASTEDISPOSALREPORTESTIMATED TOTALERRORSASSOCIATED WITHEFFLUENTMEASURENIENTS DATAPERIOD:January1,1995-December31,1995Measurement Estimated TotalError1.AirborneEffluents a.FissionandActivation Gasesb.I-131c.Particulates d.Tritium15.9%133%15.8%13.6%2.Waterborne Effiuents a.FissionandActivation Productsb,Tritiumc.Dissolved andEntrained Gasesd.GrossAlphaActivitye.VolumeofWasteReleased(PriortoDilution) f.VolumeofDilutionWaterUsedDuringPeriod5033%84%60%5.0%150%3.SolidWastesa.Atmospheric Deminerlizer (Dewatered

-HIC)b.Condensate Demineralizer/

RadwasteDemineralizer (Dewatered

-CarbonSteelLiner)c.Condensate Demineralizer/

RadwasteDemineralizer (Dewatered

-HIC)d.LiquidRadwasteFilterMedia(Dewatered

-HIC)e.RWCUFilterMedia(Dewatered

-HIC)151%15.1%15.1%1515.1%34 Measurement Estimated TotaIError3.SolidWastes(cont.)f.Ultrasonic ResinCleaningWaste(Dewatered

-HIC)g.Cartridge Filters(Dewatered

-HIC)h.Processe'd DAW(StrongTightContainer) i.Non-Processed DAW(StrongTightContainer) j.Incinerated DAW(StrongTightContainer) k,Cartridge Filters(HIC)I.Irradiated Components (Dewatered-Steel Liner)15.1%250%250%250%25.0%25.0%25.0%35 TABLE19ANNUALEFFLUENTANDWASTEDISPOSALREPORTDATANOTREPORTEDINPREVIOUSANNUALREPORTNUCLIDECATEGORYUNITFOURTHQUARTER1994A.AirborneEffluents 1.Sr-892.Sr-903.GrossAlphaCiCiCi0.00E+005.46E-091.73E-06B.Waterborne Effluents 1.Sr-892.Sr-903.Fe-553.GrossAlphaCiCiCiCiO.OOE+000.00E+006.18E-03Q.QQEi0036 SECTION3METEOROLOGICAL DATAANDDISPERSION ESTIMATES37

~'

METEOROLOGY ANDDISPERSION DATAMeteorological datahavebeencollected attheSusquehanna SESsitesincetheearly1970s.Atthepresenttime,themeteorological systemisbasedona300-foothightowerlocatedapproximately 1,000feettothesoutheast oftheplant.Windsensorsaremountedatthe10-meterand60-meterelevations onthistower.Verticaltemperature differential ismeasuredwithredundant sensorpairsbetween~the10mand60mlevels.Sigmatheta(thestandarddeviation ofhorizontal winddirection) iscalculated fromwinddirection atbothlevels.Dewpointandambienttemperature sensorsarepresentatthe10mlevel.Precipitation ismeasuredatgroundlevel.Aback-upmeteorological towerwaserectedin1982.Itisa10-metertowerproviding alternate measurements ofwindspeed,winddirection, andsigmatheta.SSESmeteorological dataistransmitted totheplantcontrolroom,Technical SupportCenter,andEmergency Operations Facilityforemergency responseavailability.

Thedataisalsotransmitted viatelephone linedata-link tothePPBLcorporate computerinAllentown.

Dispersion modelingforeffluents fromnormaloperation ofSSESisdoneusingXOQDOQ,astraight-line airflowGaussianplumemodeldesignedtoestimateaveragerelativeconcentrations.

Tgemodelwasdeveloped inaccordance withRegulatory Guide1.111.Calmperiodsaredistributed asthefirstnon-zerowind-speedclassintheinputjointfrequency distribution file.XOQDOQusesterraincorrection factorstoaccountforthetemporalandspatialvariations intheairflowintheregion,sinceastraight-line trajectory modelassumesthataconstantmeanwindtransports anddiffuseseffluents inthedirection ofairflowatthereleasepointwithintheentireregionofinterest.

TheSSESterraincorrection factorsweredetermined bytheratiooftheresultsofthestiaight-line modeltothepuff-advection model,andareincorporated intoTable22.38 TABLE20ANNUALEFFLUENTANDWASTEDISPOSALREPORTMETEOROLOGICAL DATAAVAILABILITY DATAPERIOD'995 PARAMETER PERCENTOFVALIDHOURSDURINGPERIOD1.Windspeeda.10-MeterSensorsb.60-MeterSensorg75gg42.Winddirection a.10-MeterSensorsb.60-MeterSensorgg4995%I3.Indicator ofAtmospheric Stability (PrimaryTower)a.Temperature Differential between10and60meters(Delta-TA) b.Temperature Differential between10and60meters(Delta-TB) c.SigmaTheta@10Metersd.SigmaTheta@60Meters989%g87501o/*50.1%*4.Percentofhoursforwhichvalid10-meterwindspeed,10-meterwinddirection, andtemperature differential wereavailable.

g6g5.Percentofhoursforwhichvalid60-meterwindspeed,60-meterwinddirection, andtemperature differential wereavailable.

988%'Classification ofatmospheric stability bysigmathetaisthesecondary methodusedatSSES.Theinputresolution oftheClimatronic computerisreducedsignificantly bydigital-analog conversion.

Halliburton-NUS beganusingthesigmathetavaluesfromCampbell's dataloggers effective July1,1995.39 FlGURE6CALMO.O.000ANNUAL883808S.mmH3WINDDIRECTION FREQUENCY (PERCENT)

~~MEANWINDSPEED(MI/HR)].O-METER ANNUALWINDROSE-1995 FIGURE6CALMO.O05ANNUAL8707OBS.EKEWINDDIRECTION FREQUENCY (PERCENT) tZi~MEANWENDSPEED(MI/HR)60-METERANNUALWINDROSE-1995 Figure7ESPASQUILLSTABILITY CLASSPREVALENCES DataPeriod:1995BasedonJoint-Frequency Distributions at10Meters(8487HourlyValues)Neutral411%SlightlyUnstable4.6%Moderately Unstable3.5%VeryUnstable5.3%VeryStable7.1%SlightlyStable27.1%Moderately Stable11.3%42 Page1of10JTABLE21JolNTWINDFREQUENCY DlSTRlBUTlON BYSTABlLlTY CLASSPENNSTLVANIA POMER8LIGHTCO(PANT(PAL)-Susquehams SteieElectricStetion1/26/1996 TINEOFDAT:13:51:57PROGRAHIJFDVERSION(PC-1.2PAGE621995PrietaryTouerData-33-FootLevelSITEIDENTIFIER:

DATAPERIODEXAHIKED:

1/1/95-12/31/95STABILITY BASEDMINDNEASUREDMINDTHRESHOLD JOINTFREOUEKCT SPEED(NPH).SETMEEN200.0ON:DELTATAT:33.0FEETAT:.50NPHDISTRIBUTION OFMINDSPEEDANDSTABILITY CLASSAAND33.0FEETDIRECTION INHOURSAT33.00FEETNNNENEEKEEESESESSESSQlQlMQIMMNMNMNNMTOTALCALN.51-3.CO3A1-6.706.71-11.20 1.21-16.80 16.81-22.40

>22.40001073912640719410000'0000000000120713166322000000000036110000000486001164530191620000000000011216802370370000TO'IAL316321012514183847183675012453STABILITY CLASS8AND33.0FEETSETMEEN200.0STABILITTBASEDMINDNEASUREDMINDTHRESHOLD JOINTFREOUENCT SPEED(NPH)Nl:DELTATAT:33.0FEETAT:.50NPHDISTRIBUTIOH OFMINDSPEEDANDDIRECTIOH INHOURSAT33.00FEETSSQINNNENEENEEESESESSEQlMQIMMHMHMNNMTOTALCALH.51-3.CO3.41-6.706.71-11.20 11.21.16.80 16.81-22.CO

>22.4000102314116651360000000000000000024113861002310000000000000127500000027910432592'1010010000000013013351300,180100TOTAL827186851410213378451124529543 1

Page2of10TABLE25JOINTWINDFREQUENCY DISTRIBUTION BYSTABILITY CLASSPENKSTLVANIA POMER8LIGHTCOIPANY(PPtL)-Susquehama StelenElectricStation1/26/1996 TIKEOFDAY:13:51:57PROGRAH:JFDVERSION:PC1.2PAGE631995PrisaryTaterDate-33.FootlevelSITEIDENTIFIER:

~DATAPERIODEXAHINEDI 1/1/9512/31/95STABILITT BASEDOM:DELTATBETMEEN200.0MIKDMEASUREDAT:33.0FEETMIKDTHRESHOLD AT:,50HPHJOINTFREOUEHCY DISTRIBUTION OFMIKDSPEEDAKDSPEED(HPH)NNNEKEENEESTABILITY CLASSCAND33.0FEETDIRECTION INHCRIRSAT33.00FEETESESESSESSSMSMMSMMMHMNMKINTOTAL.51-3.403.41-6.706.71.11.20 11.21-16.80 16.81-22.CO

>22.400673000531151463133000000000000006220712'1121413000000000000218400011014115524428139616640200000000024331739121512542002000TOTAL162822941418141524926224161420392STABILITY BASEDON:DELTATBETQEEN200.0MINDMEASUREDAT:33.0FEETMINDTHRESHOLD AT:.50HPHJOINTFREOIEKCY DISTRIBUTION OFMINDSPEEDANDSPEED(HPH)HNKENEENEESTABILITTCLASSDAND33.0FEETDIRECTIOM IMHQIRSAT33~00FEETESESESSESSSMSMIdyllMQKMNMKINTOTALCALM.51-3AO"3.41-6.706.71-11.2011.21-16.80 16.81-22AO

%22AO315188691071231571726645104513051091001000000000~0623290008267517611379241718124000000661151800040261291C599786613311911192236956150C400000466140130009774661498111992192130800TOTAL267260290140163103183199152199341317261.1822232053C85

Page30f10TABLE21JOINTWINDFREQUENCY DISTRIBUTION BYSTABILITY CLASSPENNSTLVANIA POMER4,LIGHTC(BLPANY(PP1L)-Suaquehama SteanElectricStation1/26/1996 TIMEOFDAY)13~51!57PROGRAM:JFDVERSION:PC-1o2PAGE641995PrimarYTourData-33.FootLevelSITEIDENTIFIER:

DATAPERIODEXAMIKEDI 1/1/95.12/31/95STABILITY BASEDMINDMEASUREDLIINDTHRESHOLD JOINTFREQUENCY SPEED(HPH)BETMEEN200.0ON:DELTATAT:33.0FEETAT:.50HPHDISTRIBUTIOH OFMINDSPEEDANDSTABILITY CLASSEAND33.0FEETDIRECTION ININRIRSAT33.00FEETNNNEKEENEEESESESSESSSMQIMQIMMNMNMNNMTOTALCAN.51-3.403.416.706.71-11.20 11.21-16.80 16.81-22.40

>22.40277718039765412380000000002281852121201000011422000115.11728-3542006000012867233001361601800050140,27100126542516~32000005111000044138812267520'1440114:000000TOTAL7815624225019011814717822131421884341716.352298STABILITY BASEDON:DELTATBETMEEN200+0LIINDMEASUREDAT:33.0FEETMINDTHRESHOLD AT:.50MPHJOINTFREQUENCY DISTRIBUTIOH OFMINDSPEEDANDSPEED(MPH)HNNENEENEESTABILITY CLASSFAND33.0FEETDIRECTION IHH(AIRSAT33.00FEETESESESSESSQIQIMSMLIMHMNMNNMTOTALCALM.51-3.403.41.6.706.71-11.2011.2116.8016.81.22.40 i22.402181047'52000000000003601904730000000063100003128302211212000000000~0000000190210086080100295000000200000000000000,000.0000TOTAL1123109.40719364~32293234170310295845

Page4of10TABLE21JOINTWINDFREQUENCY DfSTRIBUTlON BYSTABlLITY CLASS'PENNSYLVANIA POMER8LIGHTCNIPANY(PAL)-Susquehama SteanElectricStation1/26/1996 TINEOFDAY:13:51:57PROGRAM:JFDVERSIDHIPC1.2PAGE651995PrissryTeerData-33-FootLevelSITEIDENTIFIER:

DATAPERICOEXAHINEDI 1/1/95-12/31/95STABILITY BASEDMINDMEASUREDMINDTHRESHOLD JOINTFREOUENCY SPEED(HPH)STABILITY CLASSGAND33.0FEETOH:DELTATBETMEEM200.0AT:33.0FEETAT:.50KPHDISTRIBUTION OFMINDSPEEDAMDDIRECTION INH(RIBSAT33.00FEETNHHENEEHEEESESESSESSSMSMMSMMMNMNMNNMTOTALCALH.51-3.403.41-6.706.71.11.20 11.21-16.80 16.8122.40>22.40112'501300000000000'3583600008210000215240000000000000000000020100100000000000000000000015640'(.420000000000000000TOTAL1137839483215242110001606STABILITY BASEDOH:DELTATBETMEEH200.0MINDMEASUREDAT:33.0FEETMINDTHRESHOLD AT:.50NPHJOIN'IFREQUENCY DISTRIBUTION OFMINDSPEEDANDSPEED(NPH)KNHEKEENEESTABILITY CLASSALLAND33.0FEETDIRECTIOH INHRIRSAT33.00FEETESESESSESSSMSMMSMMMNMNMMKMTOTALCALH.51.3.403.41-6.706.7111.2011.21-16.8016.81-22.40

>22.40611811301200158454277271876610000010185741886410130200002685012000240"21913217940441800002141867670056.000101404101833632335611307002011013965401687984,10415119150000114363499286113216562532401100TOTAL3845237911216653330413450483653930576338218258270848746 Page5of10TABLE21JOINTWlNDFREQUENCY DlSTRlBUTlON BYSTABlLITY CLASSPENNSYLVANIA POKER8LIGHTC?NIPANY(PPCL)-Susquehama SteeaELectricStation1/26/1996 TIHEOFDAY?13?51?57PROGRAM?JFDVERSION?PC-1.2PAGE661995Prie?eryTo??erData-33-Foot.levelS!TEIDENTIFIER?

DATAPERICOEXAHIKED?

1/1/95-12/31/95ANNUALSTABILITY BASEDDM?DELTAT'ETlJEEN200.0AND33.0FEETMIKDMEASUREDAT:33.0FEETHINDTHRESHOLD AT:.50MPHTOTALMLNBEROFOBSERVATIONS?

8760TOTALMQOIEROFVALIDOBSERVATIONS?

8487TOTALNIRGIEROFHISSINGOBSERVATIONS:

273PERCENTDATARECOVERYFORTHISPERIOD?96+9XHEAHMINDSPEEDFORTHISPERIOD?"4.9HPHNINSEROFOBSERVATIONS VITHBACKUPSTABILITY:

TOTALM?RU?EROFOBSERVATIONS KITHBACKUPDATA:00PERCENTAGE OCCURRENCE OFSTABILITTCLASSESA8CDEFG5.343.484.6241.0627.0811297.14~DISTRIBUTION OFlllKDDIRECTION VSSTABILITT HNKENEENEEESESESSESSQIQlUSUUIJKMMUNMUCALHA8CDEFGTOTAL3168271628267260781561123113384523321012186'229429014016324225019010940719378394837911216'535.145141418103183118147643221533041318101419917829245038'7183213378152492152199341221314218323417421483653930674562317840157650.01120241602611820341703110003382181047 V

Page6of10TABLE2$JOINTWlMDFREQVEMCY DfSTRlBVTlON BYSTABlLITY CLASSPEKNSYLVANIA POMERCLIGHTC(N(PANT(PAL)-Suaquehsma SteanElectricStation1/26/1996 TIKEOFDAT:13t54(54PROGRAH:JFDVERSIONIPC1.2PAGE621995PriearyTouerData-200.FootLevelSITEIDENTIFIER-DATAPERICOEKAHIKEDI 1/I/95-12/31/95STABILITY BASEDMlKDHEASUREDMINDTHRESHOLD JOINTFREGUENCY SPEED(HPH)Ok:DELTATBETMEEN200.0AT:200.0FEETAT:.50HPHDISTRIBUTION OFMlkDSPEEDANDSTABILITYCLASSAAND33.0FEETDIRECTION INHOURSAT200.00FEETNNKENEEKE~EESESESSESSQIQlMQIMMKMNMKNMTOTAL'ALH.51-3AO3.41-6.706.71-11.20

'1.21-16.80 16.81.22AD>>ZZAO00042251031011242203500000000000014000001026988194121702100D00000017300D1754820005747600071500000100000867204153251TOTAL21939955111429461561148001458STABILITY BASEDMINDHEISUREDMINDTHRESHOLD JOINTFREQUENCY SPEED(HPH)ON:DELTATAT-200.0FEETAT:.50HPHDISTRIBUTION OFMINDSPEEDANDSETMEEK200.0STABILITY CLASS8AND33.0FEETDIRECTIOH IkHOURSAT200.00FEETNkNEkEENEEESESESSESSQIQlMSMMMKMNMNNMTOTALCALN.51-3.403.41-6.706.71-11.20 11.21-16.8016.81-22.40

>>22.40022718126000002236000000001226600000111136'41101002010141291423270-000610010~010021100000013055114237601001TOTAL112621585910123569601723429748 Page7of10TABLE2lJOINTWlNDFREQUENCY DlSTRIBUTlON BYSTABlLlTY CLASSPENNSYLVANIA POMER8LICHTCOMPANY(PPAL)-Suaquehamn SteieELectricStation1/26/1996 TIKEOFDAY:13:54154PROGRAM)JFDVERSION(PC1+2PACE631995PriaarYTaerData-200-FootLevelSITEIDENTIFIER:

DATAPERICOEXAKIKEDt

'1/'I/9512/31/95STABILITY CLASSCAND33.0FEETSTABILITY BASEDMINDMEASUREDMINDTKRESKOLD JOINTFRNUEKCYSPEED(MPH)BETMEEN200,0OM:DELTATAT:200.0FEETAT:.50KPHDISTRIBUTION OFMINDSPEEDANODIRECTIOH INIKXIRSAT200,00FEETHKKENEEMEEESESESSESSQISMMQIM~MKMMMNKMTOTALCALM.51.3.403.41-6.706.71-11.20 11.21-16.80 16.81-22.40

%22.400052428924517910760000000000000213446020000217971401001052011341130'0001000019662129031157V6164311184121)010600018400004TOTAL14312358913142218688338171220395STABILITY BASEDOl:DELTATBETMEEN200.0MINDMEASUREDAT:200.0FEETMINDTHRESHOLD AT:+50KPHJOINTFREOUEHCY DISTRIBUTION OFMINDSPEEDAMDSPEED(KPH)MNNEKEENEESTABIL'ITYCLASSDAKD33.0FEETDIRECTIOH IHHOURSAT200.00FEETESESESSESSSMQIMQIMMNMNMMKMTOTALCALM.51-3.403.416.706.71.11.20 11.21-16.8016.8122.40>22.40438489012413131341100605129835944124342320410301000254220600352929445546468357'12131832600406046350021713469102,1515917445214753401625123134138102514956815.~000438723878121145762,6802140011TOTAL20829429014810793140182157181321457333214216212355349 Page8of10TABLE21JOINTWlNDFREQUENCY DlSTRlBUTlON BYSTABlLlTY CLASSPENNSYLVANIA POMER8LIGHTC(NIPANY(PPCL)-SIFJeh~St++0ElectricStetim1~/ITINEOFDAY:13:54:54PROGRAH:JFDVERSION(PC-1.2PAGE641995PrienryToeerDote-200-FootlevelSITEIDENTIFIER:

DATAPERI(OEXAHINEDJ 1/'I/95-12/31/95STABILITY BASEDMINDHEASUREDMINDTHRESHOLD JOINTFREOUENCY SPEED(NPH)DKtDELTATBETMEEN200.0AT:200.0FEETAT:.50HPHDISTRIBUTION OFMINDSPEEDANDNKNEKEENEESTABILITY CLASSEAKD33.0FEETDIRECTION INH(RJRSAT200.00FEETESESESSESSSMQJMSMMMKMNMNNMTOTALCALH.51-3.403.41-6.706.71-11.20 11.21-16.80 16.81-22.40

>>22.402372114694641170994219265740103491322021010000037421437018131100435236623064122789304279943450311242510651161014'128132311516429160034'0000300003597980518682224813606TOTAL943102671237153101132214254310293572735332374STABILITY CLASSFAKD33+0FEETSTABILITY BASEDMlNDHEASUREDMINDTHRESHOLD JOINTFREOJENCY SPEED(HPH)ON:DELTATBETMEEN200.0AT:200.0FEETAT:50HPHDISTRIBUTION OFMINDSPEEDANDDIRECTIOK INHOURSAT200.00FEETNNNENEEKEEESESESSESSQISMMSMllMNMKMNNMTOTALCALH.51-3.403.41-6.706.71-'11.2D 11.21-16.80 16.81-22.40

>>22.401666107593733203631885941D10000000000000'3671000292518682133300000000018351D000010402224313510213545811194002751100000120000000o0oooooTOTAI.552781747S45443S3642635743635"997650 th Page9of10TABLE21JOINTWINDFREQUENCY DISTRIBUTION BYSTABILITY CLASSPENNSTLVANIA POMERtLIGHTCNIPANY(PPSL)-Susquelema SteanElectricStation1/26/1996 TIKEOFDAY:13:54t54PROGRAM(JFDVERSION:PC1.2PAGE1995PrieiryTamrDate-200-FootLevelSITEIDENTIFIER:

DATAPERIODEXAMINEDt1/1/95-12/31/95STABILITY BASEDMINDMEASUREDMINDTHRESHOLD JOINTFREOUENCY SPEED(KPH)OK!DELTATBETMEEN2000AT:200.0FEETAT:.50KPHDISTRIBUTION OFMIKDSPEEDNiSTABILITYCLASS0AND33aOFEETDIRECTION IMNOURSAT200+00FEETKNKENEEKEEESESESSESSSMSMMSMMMKMNMCALM.51.3.403.41.6.706.71.11.20 1.21.16.80 16.81.22.40

>>22.4033662322429159658823000000000000000000285100017'38'0200000081700001C17200011000'0000006111424~3~000:0000000000TOTAL34198127403234252325332161151STABILITY BASEDON:DELTATBETMEEN200.0MIKDKEASUREDAT:200+0FEETMINDTHRESHOLD ATt,50KPHJOIN'IFREQUENCY DISTRIBUTION OFMINDSPEEDAMDSPEED(KPH)MKNENEEKEESTABILITY CLASSALLNN33.0FEETDIRECTION IMHQNSAT200.00FEETESESESSESSSMSMMSMMMN'MNMNKMTOTALCALM.51.3.403.41-6.706.71.11.20 11.2116.8016.8122.40>>22.4046212350219144158637336135901682462134828455838612134020000013079267101251131101161051181622188413614519119316598C10187031070253361C23924131863761788112121064301811561356062860'1194741163148547913000170226982738126922923TOTAL4181156941.408276243"3374115016301D021056460264276280865951

Page10of10TABLE21JOINTWINDFREQUENCY DISTRIBUTION BYSTABILITY CLASSPENNSYLVANIA PONER8LIGHTUNIPART(PPSL)-Susquehanna SteanElectricStation1/26/1996 TINEOFDAY:13:54:54PROGRAH'FD VERSIONFPC1.2'AGE661995PriaeryTouerData.200.FootlevelSITEIDENTIFIER:

DATAPERIODEXAHINED:

1/1/95"12/31/95 ANNUALSTABILITY BASEDON:DELTATBETNEEH200+0AND33.0FEETllINDHEASUREDAT:200.0FEETIIINDTHRESHOLD AT:,50HPHTOTALNQISEROFOBSERVATIOHS:

8760TOTALNNBEROFVALIDOBSERVATIONS:

8659TOTALNINBEBOFHISSINGOBSERVATIONS:

'101PERCENTDATARECOVERYFORTHISPERIODt98.8XIIEAMMINDSPEEDFORTHISPERIODs7.4HPHNat&EROFOBSERVATIONS MITHBACKUPSTABILITY:

TOTALNOSEROFOBSERVATIONS IJITHBACKUPDATA:00PERCENTAGE OCCURRENCE OFSTABILITY CLASSESA8CDEFG5.293434.5641.0327.4211.277.00NNNENEENEDISTRIBUTION OFHINDDIRECTION VSSTABILITY EESESESSESSSMQlllQIIINNNNNNNN'CAUIABCDEFGTOTAL2193911262114312320&29429094310267552781743419&1274181156941955~1481237840408558589107937153454432342762431191314010138253371429101214,22182157132214364223254115D14615635691868181321254,31063573321630100211486017'833845733329357436611056460002317122142162735351526427604020~021203309010280052

'

Page1of15TABLE22AVERAGEANNUALRELATIVECONCENTRATIONS 8>avaaaa~

Ct~tlaacalaCcaclva~NO&i'LEVEL

&ELfdCECZ&CECTED INCOCOTtl&ll&&ECICCI&ATNN VCI&0CTCCI6LTf~lolOAAW1E6CTI&$&EL&TIVEOETNITIOI CE&NITi&f4~.ZIATEl)toOOICTCCTCa&lb/INI CECTC&$DIClCTIOa~OIST6&CES 1$&ILESTCCVClif1,001.50g.oo2.503AO3.50i,DC4.154E082.1QfN1,1)TE.N4,$7IE093244E09IOITE09T,Z)6EM$>)17%10$.726E104.2)CE10).ZIICIC&.WE08'Z.hof>CO I.LOM00$,7$$%494.57IE092Tgbf091&IZE09ITOTE09$,0$4E~105908E104.LODE~IC1,02)E.07 3,50if.o&

Z.DZLENI,ZLM.N4.139%09)A5if'092,42M09IQh09I~147%>09$.477t104AOCC~ICI.Qdf075~107t'$03.17ot0&Z,OBEN1>OZCE>N4.540f094&LE>0$2>'llof09Z.N'091.5)9%09I.ZDM00IDZIE>073>496E0&I$0)f'NI,NOf084.974EW2.916E09I.OOLENI2672M$.777%104ACZE10$.1)itIC5.7QENT.OLSEN1OLDE>N4.1700403,11M%1$22C+1'l)M09$.07M105>'740%104.410%10).4)OE~IC&A5ifOS2.$$9E0$1,)dbf00O.ZZM094AQE~Z.ZQC091,&ill091,268%099,)04E~107.092E10$.$2$EIO7,21MN2.$96E'NlAL)t>089,$2)t'094.$)M492.7QE091ALDE09IZbdf'090.77M104.972%10$.647E~107.151E082.)96E'N1.259E087,)OCCW),$)df'092422%'09T.TOZE>09 I~Lddf09$,)$0f104.5QE'10$.2$0E'10aac9.4$9E.N3.)iotNI.&)bf081.1$7t805.7)OEM3.$9N492.505t091.724%091.241E099.779E~10TAQIIDac'1,577E074,7Qf'N2.$)bf081,)ggfOI7>$$&EN4,9)CE093.457E09gABE09T,TCOE091,4BE09IITIC'09lal9>)l)f'08 3~IQC'081.492E'08 1.071%005.222C>09 3306E'092.3)OE'09 I>bodt>09 I2&CC'09'I.Dill09&A)CC'IOC$.)ZTE.NI.OOTC>N9329f095.2&it092.$49EWI.S)TE>09 I.DBC097.1)CE>105.1)lf10).99)f10)~ITVE'IOEll40)IE'0$1,29&t'N4.71il'09

).79OE'09 I77lf'09IOIbf'09bAQf104,459%>IO

),%TOE'Io2.)NE~101.709E10CCi>312E081,444CN7A&M'094,&ZM092,2&M09I,mfN$4)ZE>10$,$60%103,499%102QIE10IOoll'10SM4.716%.NIA49E.NLSSM'09).NIC092,)$9%NOIAill099.754C104.)hf10iAOIC~ID).ZLZE102.)IOElo0ICCCIIOVolclbaccS IaOIL&8Iaoasills.oor.soIo.ooIs.oozo.oo2$,00)D.ooB.ooio.oo4).ooso.oo8'.$)bf10I,COTE.IO 4.906%'ll I0)ZE'll4>tME>12IA4IE'IZd.hlfI)Z,&ICE.T)

I~752EI)1.05of.1)

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$.12OE~I)4.)gif~1$3.$)OE0VTvO.dhf1D4.IZM'ID2,0)M104.90)E.IT 1,97&t'll 4,)OIE12).009E'l2 T>OTIC125.SLOEI)2.214EI)'I$09E'I)L.IZZE10IABE~10$.076E~11I,9)IE117.17IE121.7&ll12$.952C.Q2,Clif0I,690fI)$.9)IEIi4.$57%Ii2>TQC10I,ZDM'ID4.229E~11'IAQE117,4$0C122,4'IOE~12I0)gf12'1,45glI)7,529EIiZAobl14I,obifNaViACIE101,99M10I,DSLEIo)AOZE111,260C113,491C~121,5BE12)ABtI)IA&LCQ7,)gbfIi4.IQC~IiiAL9C~102.202%'Io I.LL&c10)A14E~11I>Bdf'll4.049E>12 22$4t'IgI~TCCE12&472lI)),ZCOE~I)2.477%I)4$)ZEloZ.TQE~10I)CDE'IO3.)hf11I,49MI'I4,109E~IZg,QIE'12'9,211EQ4,9)CE0Z,ZODE'I)

I,796EI)aal4.44LE103.029%101.5LSE~ID4.211E~111.699E115.497%122.9)LC12I.ZLSE.IZ 7ALCEI)6.14LE~I)).)99E0VE9.46&E10LAOTE>102.)ibc100.009%~113.60)E11OA)il124.90)E~12Z.OLbf12I~147t'125,9)IE'I) iA41E'I)lac7libf10)A4)C102.11M.IO9,519%IIL.QTE11Z,BSE111,1&If~115.069%~122.956E~121.522E'l2 I.ZLZE12lZAOIE101.210f>10 4.$$9EIlZ.ZTIE111.072E~115.140C~122.44M12$.92if~I)$.011E.'I)

ZA&MI)Z.ollfI)ELII.)L&E105NCE>112782%'ll9959E124.$7$E~122494C12I107%'llZ,CTCE~I)I.LTZE'I) 59$&E'lliAQE'lllcIAC)L105,0&)E'll 2,SIZE111.02)E113.9$6E12I~I96E'125,5iif'I)

IA92fI)&AZTE'll2,)SOf'll I.OICE'lL 8511.797l'lo~.406l~11).Li)l~'ll1.179%~114.721T121Sibf127)CLE1)2,772EQI,SiofI)7,)TTEli4.02)cIiacid'LITE ocaoCITIIaa alavalildllIaZI~IIaaavls)CccloalsccavaIbcaaoaaICL I~llIL%8OILCCTIoa

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$.664K.073.253EDl3.57CE.07 3.284E.OT 3.050K.OT 3.9$CE072>dlREOT1.61$EDl6.S5$EN3.956E056.342E.N2.INK.077345K072AZSE>OT1.416E.07IS$5E071.$09E.Ol1>NIE07I7HE07I316KOT7TOBE062.NIEMSEQIKNIBIAXOARIES INMILKS34.Cs5~10lb.206.5$6E09I651K05C.54&E051.52FE074.635K083.1676.05 3.SDSE.06 3.369K053.791E053.800E.M3.232E062.C03E>05 6.922E.D9 20.308.991E~102.643K~099220E09'.521E066.2NK095.734K.09 5.$03E.09S.QYE.O9r.ORQK-09 6.3856.09 S.SOSE.09 7>131E091.673E.09 2>006K~105.424E~102.dlDE095.300E09'1.1DCE097.613E~107968E101.SORE09I.SOCK091.534K091161E092.039K094.06&E107.701K~11I.CSBK~IOI151E091.346K>09 2651E~109.239K111.539E~105.3676103.663K105>621EID3539610&.HCE.IDI~166E1030F4040.5068 Page7of)5TABLE22AVERAGEANNUALRELATIVECONCENTRATIONS ESE9.8438.07 3.13SE07SE1.009E063.509K07SSE1.250K064.137E07VENTANDBOILDINGPARAHETERS:

RELEASEHEIGHT(NETERS)DIAHETER(HETERS)EXITVELOCITY(H/SEC)1.256K071.413E.07 1.791E07960F00.00ELEVATEDLESSTHAN+000NIXEDBETOKEN000ANDCROWDLEVELABOVf+000ATTHERELEASEHEIGHT:VENTRELEASENCOEVINOSPEED(HETERS/SEC) 6.605K083.867E086.781E083.723E089.3ME08,5.189E08REPVINOHEIGNT(NKTERS)10,0BUILDINGHEIGHT(NETKRS)d1.3BLDG.IIIN.CRSoSEC.AREA (SOeHETERS) 2575+0NfATENISSIONRATE(CAL/SEC) 0ATTHEEAASIXIED MINDNEIQlT(10+0NKTERS):,

VENTRELEASEIkefIIINDSPEED(llETERS/SEC)

ISTABLECOSITIONS ELEVATEDLESS'INAN000~000INIXED&KTNEEN,DOO AND,OOOGRRINDLEVELABOVE,000 VINOSPEED(HETERS/SEC)

ONSTABLE/NEIITRAL CONDITIONS LKSSTHAN,000BKTIJKEN.000AND,000ABOVE.000Io432E083,198K098.177K101671K~10.3.'513Ell1.289K082.d54K094.4$9E-TO7.6$6E-111.575K-ll 1.8348~05 3.763E096.665E.10 1.345E~103.912K1159

Page8of15TABLE22AVERAGEANNUALRELATIVECONCENTRATIONS SVtqvt(INIVIN StmaEINCtl'IC StNtlOnCRIRNOLEVELRELEASE19952<<tbbDAYDECAY,IROEPLETED CORRECTED FOROPENTERRAINRECIRCULAYIOI USINGSPECIALTERRAINADWSTNKNT fACT$ANNUALAVERAGECNI/O(SEC/HETER Cteao)DISTANCEINIIILESSECTOR.250.500.7501.0001.500<<2.0002.5003.0003.500C.DQQ4.SQOSSSVSVVSUUWll.NVNNVNNENEEN'fE~ESESESSE1.10&E:05 3.926E062.241K061A4TE067.519E074.7?la<<07 3.314E.07 2.30&E<<07 l.i5bE07I.tref<<07I.QQIK.D?

2.100K-OS T.otra-ob C.ob&E.O&

2.560K061.453K069.597K.OT 6.840E.OT C.rbn073.395EOT2.600K07Z.pt(a-or 4.&85K05IA&CK-0$SA&SE06S.&boa.o&

3.13ZE0&2.052K0&1.484E061.075E06S.OCTK.QT 6.25&E.OT 4.90&a071.1CTK.04 3.561E.OS 2.1QE.OS1A45E.OS8.103K055.645K06C<<JOIE.O&

3.150E062.364K06192tE.061.593E.D&

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5.724K06JAZJK062.0405.06 1.311K069.25n.ord.890E075.320K074.242E073.4QE.D?2.303f.os 7.945E<<ob co?005.06 3.CDIE.O&

1.822K061<<IQJE.O&

S.ST&a.or 6.153K074.SSTE.QT 3.78&E-07 J.204E-D?

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$.59?E.OTZ.995E-OT 1.82?E071.55EOTd.?S5E056.509K>>ob 4.586E05J.?30K.N4dldf061711E<<061000K066540E073<<JSSE0720?0E071413f079452ENb<<SQE05<<AOSE053<<S?9E05$.087K.oeZ.(bra.o&.I.2&6K-oe T.QZEor3.004K.or 2.$2&K*a?1.?0sa-or t.wf-or0.220K.N&.TQE-Nc.occa-od ANNUALAVERAGECHI/O(SEC/HETER CUSED)DISTANCEINNILESSEARING5000750010<<00015<<00020<<00025<<DQQ3000035<<0004000045000SO000SSSVSVVSVVIAIVNVNNNKNaEREfEsaSfSlfcHI/0(sab<<ZJCEN3.619E.N1.522K'08 4.13JE.09 1.80?E<<09 6.104E~103.230K.IO I.C1&E~109.157E~115.71&E1'I4<<52?E~111.6?&E0?T.543E054.066E081.2QF.05S.S28E.00 1<<05&a~009.S4tf10J.tcca102.0(?a~108.510E-'ll 7.198E.II c.lbsa-o?

Z.OJJE-QT 1.000K-QT J.Wa-odl.sssa-ob 6.836K.00 3.8?CE-00 1.904K-00 1.334K.00 rAtoa-lo6.20n-to1.35CE066.9&Sf.Q?

3.799K0?I.oslf.o?

4.75&E051.&QE08S.bl?E093.26&E091.?03E097.525E.10 6.41SE10C.?40E.O?

2.213E071.170E.D?

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7.534E.D?

0.001E0?6,??OE0?3.&SSE.O?

1.?9&EOF1.695K'0?3.Cd?E0?d.lS?f0?2.C2of0&8.83?a0?4.82?E0?S.JSSI0?C.?10f0?C.JCQE~0?5.?NE0?4.00ZE.OT 2.257'?9.9JIE051.01?ED?Z.060K-o?

$.0?SK.O?,1.&02E<<ob5.60CE0?3.1&DE0?3.4?5E~0?3.200E0?2o073E0?3.Seta0?Z.rezf.or 1Solf076.464E083.846EN5.046K052.006K0?7.015E0?2.315(.O'1.355E.07 1.40JEOF1.449EOFIA12EOT1.725E071.2?9$.07T.stsa052:817K.OS 6<<231f001570K054.106K05l.coca-or C.264E052.9Zbf053<<ZJSKOS3.124EN3.$22E053.553E.N3.065K052<<203K05&.QJE<<005.170E102.515K007.0?JK00R.t?sf05S,etta00C.944f094.799E094.923E006.14tf00SAQE.095.02?f-00&.SNK-00'I.SStf-09 1.745E104.5$4E'IO2<<'RSOE004.201K098.901E'106.20ZE10&.sd7K10I~235K091.24&E001290E091.01?f001.525E093.655E10&A15E11115?a10S.TS&E10IOZQE091.002K106,981K11Ildtf104.1?3f.lo 3<<00?E~104.CTZE'IO 3.2285.10 5.09&E~101.031K10SEGKKNIROVNOARIKS INKILES34455.10102020.3030.40"405060 Page9of15TABLE22AVERAGEANNUALRELATIVECONCENTRATIONS ESE9821E073.121E071.246E.07 6.533E08SE1.007E063.496E.07 1.405K0/6.722E08'SE1.247E-06 4oT20E07'l.778K079.263K08VKMTAXOSUILDIMCPARAMETERS:

RELEASEHEICHT(METERS)9,60DIAMETERtkETfRS)+00EXITVELOCITYtH/SEC).00REP.VINOMEICHT(METERS)10.0BUILDINCNEICHT(NETERS)61,3BLOC.IIIM.CRS.SEC,AREA (SO.METERS) 2575.0NEATENISSIONRATE(CAL/SEC) 0ATTNENKASLNIED VIXDNEICHT(10.0METERS):VENTRELEASEIMNEVINOSPEED(ItETERS/SKC)

STABLECONDITIONS LESSTNAM000SETVEKM~000AMD000ABOVE.000IIILESSTHAN.000ISETVEKN000AMD000IABOVE.000ATTNERELEASEME!CRT:VENTRELEASEIXOEVIIOSPEEDtNETERS/SEC)

VINOSPEED(METERS/SEC)

UNSTABLE/NEUTRAL CONDITIONS LESSTNAM.000SETVEEM+000AXDF000ABOVE~000ELEVATEDMIXEDCR(AXOLEVEL3@812K08IAOE083059K097565k10Io501E>10 2867E1'I3abdOE.08 lo267f-08 2+564K094+200K~TD7.022E~111.228K~115~121E081.796K083od15E.09 6.215E.10 Io216E~103.41df~1161

Page10of15TABLE22AVERAGEANNUALRELATIVECONCENTRATIONS Svtovtkgz~

STOLENEIBCtr)cStat)on.CRIRNOLEVELRELEASE-)995LoooDAYDECAY,DEPLETEDCORRECTED fOROPENTKRRAINRECIRCULATION US)koSPECIALTERRAINADJQ5ggNT ANNUALAVERACECIII/O(SEC/METER CLRIED)DISTANCEINMILESSfCTOR~2$05QQ750I000ISoo2000Zosoo30003SOO40004$008SSVSVVSVVVMVMVNNllNNNENEENEEESESEBtf).OCIE.05 3.$90E0620028.061.270K.06 6.413E.OT 3.973E.OT 2.704E07Z,Q7$E05d.C)PE063.6$)E062.257K06)~Zbdf068.005E.07 5.592E074,437K.os

).339$.057.749K-ob 4.976K062.677E061.714K.ob 1.215K061,0878.04 3.259E05).9)df-os I.zroE05Teoorf06c.720E06JesZSK066.17OE051.QbE05931$E065,74)E062.974E06).$9)f-ob1.327E062.8$SE05B.d)3E064ASIE-062.911E.06 l.d12E061.015$.067.015$.072,8$0E.058.90)E065.))rf063.115t.06 1.744E061.095E06TAOOE072.182E.05 TeZTOE064281E~062.9OOE061.5STE~069.962E-OT Tao)bf072.112E.05 6.434K063.S78K062.203E061.26$EObB.SZOE.DT doJDTK072,C79E.OS I.C73E064.739K-ob 3,2)CK06).690$.06).)Zbf06Be245$-07)Issf055.936E06Jo359$.062.095E06).ldof06T.drBE075+SIZE07).OOCE.DS 3.31$E061.86)E061~232E-066.30)E~074.147E07J.DISK.07 6.046E062.053E061.114E066.5888.07 3.364E.OT 2.113E071.466K074.940$-06l.d)2$.068,789$-075.)TJE-OT 2.55ZE-07

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)oC)bf.)0 1.179$.102.$9$E~102.150K~10C.348E~11J.SME~11).DOCK~119004K.)23AJJE.IZ2.PIPE121.42OE.11 1.17CE112.687K.09 I.)ZDE.OO 3.69OE10IA67$.107.92$E~115.01)E~118.3'11E09JoCQE'091.20OE09SA40E10IBISE.)01.1$5f102120E089PZZE'094ZZTE092334KDO1)Tdf097724E107+DO)K)MJ.OCbf08).OREMS.JJIE09).PJbfOOT.OC4E.OO 2.130E08I.JOIE092.)OCE09)o)SOE.OO J.ICZE~10R.osbf101.628EOS7+DZSK092.504K09)+028KOO1.495E107.975E~111.844E08T2QEDO2.0QE099405K102,286Elo)oZ)lf10I71$E086,927K092.163.09I254K09b,d72E~10J.IZ4f-lo 1.696E087785EOOJ.JJIEQO1,572K0952$1E102.892K~10).QbfOb7674EOO2ASSE09)oCObf096.119E10'3.74)E101.796E~08T.lbbf.09 2.09ZE.09 I~095K.OOCebbrf102.734E.IO

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).Oosf061.)ZOE062.36.726E07l,zrof.ob 2.76of.067.257E.O6 J.lobfOb1.QCE.Ob1.776EOb1.62bfOb1.29OE'Ob1.778K061.193E066.681E.Or3.524E072.70OE~Or$.$RBKor1.209KOb3.449KObIJZZf.ob7.063Kor7.6TZK.OT 6.975f.or 6.178Eor8.113EOr5.53$EOr3.011E'07l.cb7E.OT I~34)E072.762K'Dr 6.C75for).923K.ob 7.023K~Of3.Q5E.OT4.2$)f07J.rczf-or 3.cclforCoSZOE'073.1SPE071.778K~07'7.824E.08 T.bool.ob

'I.SOSEOr3.920EOr1.23$E06CADRE072.C42E072.684KOrR.cbrt.or 2.291E072.972E072.117K.OT 1.217K074.942KM2.$14EM$.9)ZE0$1.545K~075.)TIE~or 1.7)ZEorO.OOBE081.099E071.064E071.'IIIE07'l.266E-07 9.310E085ASlE.OB2.0C4E08SKCNENIBOUNOARIES INIIILES4.$5.1010-20,4.195E.09

).062K082+862K~089.627E.082.928E081.999E.082.20CEMZo)ZJE082.397K08ZoCOCE08ZiOCJE081,$06E.OICoJTIE.OO 20304.963K101.557KDO4.988EDO1.3TDE-M3,431KDO3.12OE.OO3.012E.IS3.070KOO3.$17E093,49CE09J.OCTK093.92)E.09OoZZIK10JO.CO9.BISE-ll R.bsbf.)0

).JSJEOO2.568E095.349K.lo J.TJOE103.9IOE1072QE107JCCE10ToCQE~10seTJJE10)oo)JE09Zoofbf~10Coiso3.C33E.II 6.44$E115.009K10S.MQE10).)SCK.)0 4.04'IEF116.744E.)1 2.3S'OfF10)A96E102.C75E~101.'7'l9E-10 3.)JIE~10$.367K-))62 V

Page11of15TABLE22AVERAGEANNUALRELATlVECONCENTRATIONS 1.501E~118.32df.12 1.774E118,380K1'I3.852KII8.718E114505K102.492E103.70bf.10ESE8.811E072.87bE071.018E.07 5.149K-08 SE9.0258-07 2.995K071~147E075.293K08SSE1.118EOd3.530E071.452E077.299K08VENTANDBUILDINCPAkAHKTERSI RELEASEHEICRT(NETfRS)9eb0DIANETER(HETEkS).00EXITVELOCITT01/SEC),002.917E081,020EOS2.019K092.81'IE.OS 9.211E09I.ddbf093*9188.08 I308K08MS'.09RfPUINDNEICHT(NETERS).10.0SUILOINCNEICHT(HETERS)d1.3SLDCoNIN~CRSoSEC.AREA (SOokfTERS) 2575.0NEATEN(SRIONNATE(CAL/SEC) o0ATTHENEASUREDUIHDHEICNT(10+0HETERS)IVfklRELEASEIHXIEUINDSPEED(NETERS/SEC)

STASLEC(HH)ITIQIS LESS1NAN000kfTUEEN000AIO000AHOVE,OOO ATTHERELEASENEICH11VEkTRELEASEHCOEUIIXISPEED(NETERS/SEC)

III~000I.000AIS,OOO/~000ELEVATEDNlXEDCR(XNOLEVELLESSTHANHETMEENASOVEELEVATEDNIXEDCR(XMDLEVELVINDSPEED(NETERS/SEC)

UNSTABLE/kEUTkAL CONDITIONS LESSTNAN.000SETMEEN+000ND.000AHOVE.00063 P

Page52of15TABLE22AVERAGEANNUALRELATIVECONCENTRATIONS StbtienNRECIRCULA RELATIVEDSvvPIehacw St~ElectIIcCORRECTED FOROPENTERRAIDIRKCTIONFROISITESSQISVVQIVNVNNNKNEENEEESESESSEDIRECTION FRCHSITES'SVVQIVNVNNVNNNfNfENEEESKSfSSK.502.162E082.739E.08J.SOCE.N5,107E053.496K.N1.9496.08 2.6596.0$2.596E062.396E053.540E084.742E053.1QE.081.609E.N1,295E05'1.446E061.669E.08

.256,1$6E086.207E051.025K071.436E.071.021E075.74?Eebb b.CSCE.087.215E057.151K069.489E.N1~377E079e313E.06 5.327E.NC,OJIE064.312E05C.716E085.002.S$6E103.5OCE-10 5.129E109.675K104.122K102.7$2E'104A61E104.649K.104.552E106.46CE109.648K107.1CCE.10 2.601K101.346610I.CIGK.10 I.TOTE107.$01.009Ee10 1.3556.10 2.128E.10 4el?36.101QJE101,203K10IOOSE.IO2.202E102.7QE~103.029K~104.659E.10 3A6SE101.210E.10S.080E~11S.OQK~11b.406E~11RELATI~eeeeeeeeeeeeeeeeeeeeeeo 1.2DIRECTION 5~1SROHSITES1.165E~08SQI1.C97ENsv2.0066.06 VSv3.0Obf~06v1.84OENvvv1.054K08Nv1.567E~06NNv1.Cbtf~Ob1.ZTTE~06,NNE1.933Ee06 NK2.56?fNEKK1,7CSE'Nf9.C7OKOOEST6.606E09SK7e966EDOSSK6.95$EDOVENTANDRUILDINCPA20.30JO.COCoe503.53SE.13

$.690EIJ1.46$E.121.4$1E124.0lbf.13 3.719E.136.3096.13 1.303K~121,JOSE,IZ I.S376.12 2.S25E~126.191E.12 1,166E~124.691E.132.$$1E.133.620E~131.122E~10I.SSSE102.3?bf~104.437E101.619K101.296E102.129E.IO 2.278E102.546E103~133E~104.839K.I03A626e101,273K~105.924E116.2COE.11 7.660E~113.C60EDOC.bbbfOO6.QZEOO1.077E08S.JOOEOO3.216K~094.616E.OO 4.8$3EOO3.979KDOb.'ICSK098.201KDO$.603KDO2.7NfOO1.65CE092.C2SEDO2.$71EOORANKTERS:1.648E123.545E~125.964E~126.612Kel?2.6QE123.3?tf.12 5.136E~125.826E127176E~127.60CE1?I.CZSE~112.C94E~11S.S$6E122.575E-1216836.12Ze0696.12 1.186E13.1eJDE.I3$.1$5E~13J,DSJE135.197E143,760E1C1.0376.13 4.062K.IJ 2.666E.13 4.6$CE.13T.ttlfD1.5QE123.0Slf.13 6.207E.14 C~110K149etSJE1C5.699K.10 6.333K.IO 1.173K.OO 2.092KOO9.NJK10S.OOTK.I0OA?6E~109.142K~106.609K101.279K~OO1.64tf.OO 1.310K.OOS.27TE~10J.207E~103.8ZCK~104.6CTK.10 3.273E~104.$1$E10b.SCTK~101.215K.OO 5.219K~10J.Cblf10$.603K10$.677K~105.376K~107.919K101.173KDO6.610f103?06E~101.752E~101.9QE.102JOSE10I.?63E.DO 1.607E.OO2.Q7E094.30?fDO1.919EDOI.ZOJKDOle643EOO1.643K.OO 1.660KDO2.46?fOO3.44bf.OO2.336K091.0Clf.OO 6.6CTK.10 6.6STK109.746K10l,dZOE.II2A02E113546K~11TeblbE112.7STE.11 2.3CSE.11 4.0036.11 4.28CK.11 C.6SbE~115eS92E111.011E~109.929E~112A91E.I11.1dlfe11I1CJE111,366K11ORIANA.LEVEL RELEASE~1995TIONUSINCSPECIALTERRAINADJUSTMENT FACTCRSEPOSITIOI PERUNITAREA.(Nee 2)ATFIXEDPOINTS8TINAAOIIND SKCTORSDISTANCES INNILES.751.001.SO2.002.503.003.SOC.OO4.$01.137E.05 6.571E093.2448.09 1.917E091.256E09be317E.10 5.726E~104.t38E.10 3,211Ke101,493K05$.7856.094.5718.09 2e726E09Te61?fe09 1.189E09d.0$6E~10S.OOSE104.COOfe10 2.024EeNI.ZCJE-N6.139Ee09 3.6$4E092.4238-09 1edJTE-09 I~ICTE-DOd.477Eelo 6.405Eelo 3170E0$2035E05'I028E086340E094e341E092e910E092e023EI1539K091ROISOO1.5036.05 1.060E.05 4.97CE092.916K091.904K091,267E09d.777E.10 6.662E~105.154Ee101OCOf066170E093112K091$228091~183KDO5073K105760E104e410E'103CSOE101566E0$9223E094e6QE092e743E091$12E09IR68E099e30bf107092E10Se525E101.445E.05 9.S25E094.$538492.7428.09 1.6408091.246E096.77SE106.972E~10$.667Ee10I.?59K.N7.305E093.836E092.42?f091.702E.09 1.1668.09

$.3SOE106.546K.IO S.?50K-IO 1,6$6E05I~167Eedd5.730E093.$908092.505E.09 1.724E091.2ClE.09 9.779K10T.NJE~102.S$6E.081.S22E05T.d$6E094.950K093AS7E09ZAJSE.DO1.795KDO1eCJSE.DO 1.171EDO1,692E051.077E085,222E.DO 3,306E092330fe091.69CE091,2NE09le041E096.QdE1093?OE.DO5.266E.09 2.5496.09 I.SJOE09T.OJSE-DO 7.138E~105.1SIE~10J.OOJE.\0 3.179E-10 6.7146.09 3.790E.09 1.771E.09

1.0 16Ee09

be4$JE~104.439E~10J.ITOE10ZeJNK~101.709E107.855E.09 4.5236.09 2.253E091.333E~09$.632E~105.560E~103.699K~102eQlE.'10 1.901E~10d.9SSE095.056E092.3698.09 1.449Ee09 9.7Sbf106.S7SE.ID 4ADIE103eZC28.10 2.300E~10DISTANCES INNILES10e0015002000250030e00350040e004500SO004.900K111.032K~114.216E.12 1.36IE126.7$1E132.616K131.7$2E-13I.OSOE136.$66E147090E11ZeOOJE116NIE122TDOE12le226E123836K13ZeJbdf139S3DE1C7775E141.07ZE102.76CE~11I222K114.960E~'122ebZTE12I276E12de120E13Ce324KDJ.SJOE132.053E.IO C.903Eell 1.975E.ll 6.301E~123.089E~121.071E.12 5.$49E.132.?lbE.13 1.509K~13de074E-11 1.931K~117.171E~121.7$1E126.932K~132.d74E~131.490E13S.OSIE14Ce$$7E-'l46,229E111.8QE117650f122.dlOE121032E121,CSZED7,529E~'l42.406E1CI964E1CIeDSCE~1033026.111.260K113e491E.12 1.93'123eQSE~131.56CE~137.$26E146.143E~141.1Cbf~103.416Ee111.336Ee114.04OE122.2868.12 1.1868-12 b.dTIE.13 3.250K.I32.677E.13 1,360E~103,375fll1,493K116.169E~122.$3IE~129.2'llf134.958K~132,200fD1.796K131.545E~10C.2llf111.699E11SA97E122.934E~121.2CSE~127.446KD4.16CE~133.399K132.546E10d.509E~113.403K119A3CE~124.90SE1?2e046E~12'1.167E125.93lf13C,641E.13 2.113E109.$19E114.637E~112.35SE111.16lf115.069K~122.956K~121.522E~121.2C2f126.559K~llR.Z71E111.072E115.160E122.C43E126.924E135.011E132.463ED2.011K132.75?f.ll 9OSOE.IZC.d75E~122.CObE~121107E~1Z2edlbF~131.49tE135.956K14C.6QE.142.612f.ll 1,023E.ll 3.986E.12 1.196E~125.544E131,592K~136.827EIC2.350E1C1.918E.'lC 3.44SE~11I.ITOK114.72lf.lt 1.546Ee12

'7.364Ee13 Z.TTZEe13 1.540K~137.379K~146.0236~14VEDEPOSITION PKRUNITAREA{Ne~2151DOVNVINDSKC'IORSeeeeeeeeeeeeeeeeeeeeeeee SKCNKNTSOINDARIKS INNILKS2.3J.C5~10 Page13of15TABLE22AVERAGEANNUALRELATIVECONCENTRATIONS RELEASENEICRT(NETERs)0IANETER(NETERS)EXITVELOCITT(N/SEC)9d0~0000ELEVATEDLESSTRANNIXEDSETUEENCROUNDLEVELASOVE.000,000ANO,OOO.000ATTkERELEASENEICNTIVENTRELEASfNCOKUINDSPEED(NETKRS/SEC) lfPUINDNf'ICNT(NKTEls)TO.OSVILDINCNEICRT(NKTEls)d1o3RLDC.NINeCkseSECoAREA (SOoNKTKRS) 2$73e0NEATKNISSIONkATE(CAL/SEC) e0)ATTNENEAR%EDUINDNEICNT(10.0NKTERS)I)-VENTlELEASEN(OEUINDSPEED(NKTERS/SEC)

)STASLEC(NOITIONS IELEVATEDLESSTRAN.000NIXED~fTUEEN000AIO+000Ck(XNOLEVELASOVEe000UINDSPEED(NETERS/SEC)

UNSTASLK/NEUTlAI, CONDITIONS LESSTRAN.000SfTUffN,OOOAND000ASOVE.e000 Page14of15TABLE22AVERAGEANNUALRELATIVECONCENTRATIONS UNOEPLETED

'ROfPLETEDSVINVtNgea SteveEICCtrICStatic-GRIXNe-LEVEL RELEASE-1995SPECIFICPOINTSOFIMTEkfSTORELEASETYPEOfDIRECTION DISTANCEX/0X/0x/00/0IDLOCATION(MILES)(METERS)(SEC/CNI.METER)

(SEC/CUD.METER)

(SEC/CUK.METER)

IPERSO.IIKTER)

'ODECAY2o260DAYDECAY8.000DAYDECAYDEPLETEDSSSSSSS8S8S$SSSSSSSSSSSSSSSSSSSSSSSSSSSSSSSSSSS$SSSSITERCRNOARYSITE6IRNR)ARY SITERIXNRIARY SITEQSNDARYSITE8IRNOARYSITESXINDARYSITE8CINNIARY SITE8IANOARYSITEDIAIKDARY SITERCANOARYSITEIMRNKIARY SllK60NOARYSITERCUNOAkYSITE60UNDARYSITE6IANOARYSITE6NJNOARYRESIDENCE RESIDENCE RESIDENCE RESIDENCE RESIDEKCE RESIDENCE RESINNCERESIDENCE RESIDEKCE RESIDENCE RESIDENCE RESINNCERESIDENCE RESIDENCE RESIDEKCE RESIDENCE GARDENGARDENGARDENGARDENGARDENGARDENGARDENGARDENGARDEKGARDENGARDENGARDENGARDEKGARDENGARDENGARDENDAIRYDAIRYDAIRYSSQIQIVSVIIIANINVNNVNNKENEEKEfESESESSESSQISVVSVVVKVNVNNINNNENEENEEESESESSESSSVSVVSVVVKVNKVKNMENffNEEESESESSEfEESE,3C.42.621.221.02.62,64.5959.79~70.87~64C9.42341.0090I501.101,20.80.80.601.301.002.302.101.40.50.COAO1.101,201.901.101.201.30904.001.301.102.302.401.402.50604.504.602.70S49.d70.1315.1965.lbC9.992.1037.951.1266.1121.1398.135C.$49.1609.1448.2415.1770.1HI.1287.1287.2092.1609.3702.3361.2253.605.966.1770.1HI.3059.1770.1HI.2092.14C8.6436.2092.'I770.3TOZ.3663.2253.CDZ4.1287.7244.7405.4346.6.691E.06 9e441E.06 7obHE06lo096E05d.349E067.137E.06 6.813K06d.3SSE065.6646.06 4.6535.06 4:191E061.6968.06 I,OC1E061.792E-06 2.19CE063.653E.06 1.4SZE063.'112E.06 3.160E-06 1.267K.OS 4.976E064,885E065.391E066.210E.061.797E.063.d77K.06 7.719K074.6Hf074~C'ZIE071.764E062.377E061.702E061,2C7E062.015E.06 2.236K061.2)3E.OS 4976K.062.319E064,356K063.873E.07 1.797$.06.3.185f.06 7.719K073.938E074.C21E071.235E07Io323E061.'162E066.516E08bo266E051.076E.07 dA52E.069AZIE067ASSE.061.055E.056.306E.06 7.105E.06 d.787E066.334K06Sodddf064663K06C-179E.06 la693E061.038K.061+790K~062.192K063obSOE.Ob 1.4CTE.06 3.0968.063.131E.06 1.256K.OS 4.937E064.560K065.365E066.1ME06).763K063.6SDE.06 7.649E.07 4.661E074.CD3E.07 1.7dlf062.374E061.699E061.242E062.003E062.211K061.26CE054.H7E~062.300E06C.362K063.755EF071.783E063.167E067AC9E~073907EF074.COSE07IoZZSE07Io321fiNI1S9E066.C2SE.Me.1796.08

'.067E076.240E068.709E0666IIE069,4C2E065.$38E066.4238.06 6.115E065.736E.06 5.131E064.334E063.7C7E061.499K069.204E.07 1ASTE062.023E063AOTK.061.270E062,739K~062.d77E061.100E.OS4,290E064.330K064.779K06S.S99E061.S40E063.214K066,290E073.661K073.771E071.610EObZst96E061.$35E06II083K061.739K061.855E'06 1.105K054.290K'06 1.966E~Oe3.660EOb2.9SCE071.$COE062.765K066.290K.07 3'96E073.7/IE079.979E08I19CE061.03IE064.907E084706E066AZSE083.820E063.722f081.7d7E081A52E081.016E081.4C3E051.9)36~08 2.002E~081.566E~061.664K052.551K~M1.33SE057.$808~091.320K051.911E052.926E.0567871E09loMDE06e.7378.091.729E.08 7o5826.09 9.6096.09 1.448K051945K084.819Ei091.167E053.954K093.0$7E092.MSE09I.296KN2.056E'05 1.252KM5.767K.096.544E094.013K.09.1.737E.M7.5626.09

,3.9676.09 1.143EM6.970E104.819E09'1.001E083954K09.2ADCE092oMSEi096AOZE~10I0778058.090E.093.178E~103.038E~10S.S46E1066 Page15of15TABLE22AVERAGEANNUALRELATIVECONCENTRATIONS 4.679K084.426K081.309K071.362K.074.835K074.SOSEF073.4ME.072.946K071.740E085.719K.06 4,898K073A13E074.158E.06 6$99.6760.4185.4990.6117.8049.6760.1127.4.104.202.603.903.003.103.503.8014.002,005.004.20.704.618K084.367E081,3008.07 1,340E074.761E074.433K073.3968-07 2.888K.071.dlbE.08 5A4SE.064.739E073.S268.07 4.146E.06 5DAIRYESE5DAIRYESE5DAIRYSE5DAIRY55DAIRYSSV5DAIRYSSV5DAIRTSSV5DAIRYSSV5DAIRYSSV5DAIRYVSVSDAIkYV5DAIRYNNVSRIVERLANDS/EIC NfVENTAHDSUILDINCPlkAHETERS:

kELEASENEICHT(NETERS)960DIAHETER(NKTERS)00EXITVELOCITYtN/SEC)e003.S67K.08 3.364K.081.054E-07 1,044E073.824K073.S49E072AKSE072.263K071.074E084.718K.063.617K.072.737E.073.716E.06kfPVINONEICRT(IIETfRS)10+0RUILDINCNEICRT(NETKRS)dl.3RLDC.NIN,CRS,SEC.AREA tSO.NETEkS) 2STS,ONEATENI55IOIRATE(CAL/SEC)

.0ATTHENEASUREDVINDkEICNT(TO+0NETERS)IVKNlkELEASENtefVINOSPEEDtNETERS/SKC)

STARLECQSI7IOISLKSSTHAN,000SETVEEN+000AND+000ASOVE,OOO ATTHERELEASEHEICHI:IVENTRELEASEIHOEVileSPEED(NETKkS/SEC)

IELEVlTEDLESSTHAN+000INIXEDSETVEENoO(mlND000fCk(XHmLEVELASOVEe000I2.167K-10 2.037E~107A74E104.486E~101,189E09lo095E098.052E.10b.dSTE~102.609E-116.33)K.094e121E-106.386K-ID 2.8SSE.08 VINOSPEED(Nflfkk/SEC)

UHSTASLE/NEUTRAL C(WDITIONS LESSTHlN.000RE)VEEN.000AHD.000ASOVE00067 SECTION4DOSEMEASUREMENTS ANDASSESSMENTS 68 RadioloicaIImactonManSamplingandanalysisofairborneandwaterborne effluents wereperformed inaccordance withthefrequencies, typesofanalysis, andLowerLimitofDetection (LLD)outlinedintheSSESTechnical Specifications.

Radioactive materialwasdetectedinsomeoftheairborneandwaterborne effluentsamplesanalyzed.

Dosecalculations usingmeasuredeffluentactivitylevels,meteorological datafromthecurrentreporting periodandquarterly averagedriverflowdilutionfactorsresultedinestimated dosestoindividuals atlevelsbelow.10CFR20and10CFR50,AppendixIlimits.Directradiation resulting fromplantoperation, asmeasuredbyenvironmental thermoluminescent dosimeters locatedaroundtheplantcontributed amaximumof4.23E-03mrem(measured atTLDLocation11S3)attheProtected AreaBoundarysouthwest oftheplant.Themaximumorgan/total bodydose(childlung,1.1milesWSW:Table26)fromallairborneeffluentis1.27E-01mrem.Themaximumorgan/total bodydosefromliquideffluent(adultGl-LLI:Table24)is1.00E-01mrem.Ifitisconservatively assumedthatamemberofthepublicreceivesthemaximumtotalbody/organ dosefromliquidandgaseouscombinedwiththemaximumtotalbodydosedetermined fromdirectradiation, theresult(2.31E-01 mrem)is(1%ofthe40CFR190limitof25mremtototalbody/organ (exceptthyroid).

Dosestoamaximally exposedmemberofthepublicfromwaterborne effluents arecalculated forfishingestion andshoreline exposureattheplantoutfall,anddrinkingwateringestion atDanville, PA.Sitespecificparameters usedinthecalculations fortheDanvillereceiver, specificforactualaverageblowdownandriverlevelineachquarterandtheentireyear,areshowninTable23.TABLE23SITE-SPECIFIC PARAMETERS USEDFORLADTAPIICALCULATIONS (DANVILLE RECEIVER)

FOR1996PARAMETER CoolingTowerBlowdown(CFS)AverageNetRiverLevel(ft)(1)DilutionFactoratDanville(2)TransittimetoDanville(hr)(2)ENTIREYEAR17.35.3284.132.3(1)NetRiverLevel=Depth(ftaboveMSL)-483'2)FromODCIVITable5-469 I

Summaries ofmaximumindividual dosesresulting fromairborneandwaterborne radioactive effluentreleasesaregiveninTable24.Meteorological datafromSection3wereusedtocalculate thedosefromairborneeffluents.

Technical Specification 6.9.1.11requiresassessment ofradiation dosesfromradioactive airborneandwaterborne effluenttomembersofthepublicwithinthesiteboundary.

Therearenosignificant exposurepathwaysfromwaterborne effluents intheseareas.Onsitedosesareassessedrelativetooffsitedosevaluesandareadjustedforappropriate dispersion andoccupancy factors.Summaries of.thecalculated maximumonsitedosesresulting fromairborneeffluents arepresented inTables25through26.70 TABLE24SUMMARYOFMAXIMUMINDIVIDUAL OFFSITEDOSESANDDOSECOMMITMENTS TOMEMBERSOFTHEPUBLICDATAPERIOD'/1/95 TO12/31/95EFFLUENT

':A"GEGROUPAPPLICABLE

'ORGANESTIMATED MAXIMUMDOSEMREMLOCATIONDISTAFFECTEDMILESSECTORPERCENTOFLIMITLIMIT(MREM)~~~Liuid'iuid'EENTOTALBODYADULTGI-LLI2.14E-021.00E-010.711.0010NobleGasNobleGasNobleGasN/AN/AN/AAIRDOSE(GAMMA-MRADAIRDOSE(BETA-MRAD TOTALBODY7.10E-039.10E-034.69E-031.101.101.10WSWWSWWSW0.070.050.091020NobleGasueaudculasN/ASKINCHILDLUNG1.24E-026.27E-021.101.10WSWWSW0.080.421515"'Estimated doseisbasedonasitetotalactivityrelease."'10CFR50,AppendixIlimitsareintermsofmradormrem/reactor-year.

"'Dosesfromliquideffluentareestimated fromfishingestion andshoreline exposureatthesiteoutfallandfromthedrinkingwaterpathwayatDanville, PA.AIRBORNEPATHWAYSANALYZED:

0.40(SE):PLUME,GROUND,INHALATION; 1.10(WSW)~PLUME,GROUND,VEGETATION, INHALATION; 2.00(WSW)DAIRY:PLUME,GROUND,VEGETATION, COWMILK,INHALATION WATERBORNE PATHWAYSANALYZED:

FISH,DRINKINGWATER,SHORELINE Themaximumcalculated dosefromall1995SSESwaterborne effluent(combined pathways) was1.00E-01mrem(ADULT,GI-LLI).Themaximumcalculated dosefromall1995SSESairborneeffluent(bothunits)at0.40miles(SEsector)was1.22E-02mrem(TEEN,LUNG).Themaximumcalculated dosefromall1995SSESairborneeffluent(bothunits)at1.10miles(WSWsector)was1.27E-01mrem(CHILD,LUNG).maximumcalculated dosefromall1995SSESairborneeffluent(bothunits)at2.00milesSW)was7.26E-02mrem(CHILD,LUNG).71 DOSESTOMEMBERSOFTHEPUBLICWITHINTHESITEBOUNDARYSSESTechnical Specification 6.9.1.11requiresthattheAnnualEffluentReleaseReportsincludeanassessment oftheradiation dosefromradioactive effluents tomembersofthepublicwithinthesiteboundary.

WithintheSSESsiteboundarytherearethreeareaswhichareopentomembersofthepublic(SeeFigure8):~TheSusquehanna Riverlands Recreation Area/Energy Information Center~Residences inthesoutheast andwestsouthwest sectorsIntheareacomprising theRiverlands recreation area,whichsurrounds theEnergyInformation Center,threepathwaysofradiation exposurecanbeidentified; plume,groundandinhalation.

Therearenosignificant exposurepathwaysfromwaterborne effluents inthisarea.Thereareapproximately 100,000visitorstotheRiverlands/Information Centercomplexeachyear.Fordosecalculations, thevisitorstaysintheareaforonehour.UseoftheGASPARcodeyieldscalculated dosesfortheRiverlands areaforthereportperiod.Thesedosesarethetotaldosesatthelocationfromgaseouseffluents duringthereportperiod.Inordertocomputedosestomembersofthepublicwhostayforonlyshortperiodsoftime,thesedosesareconverted todoserateswhichareaveragesfortheentireyear.Takingintoaccounttheestimated 100,000person-hours ofoccupancy, thecollective (person-rem) dosesshowninTable25arecalculated.

Calculated dosesforresidences withintheSSESsiteboundaryforthefollowing sectorsarepresented inTable26.~southeast (0.40miles)'westsouthwest (1.10miles)72

'1

.FIGURE8AREAS.WITHINTHESSESSITEBOUNDARY, OPENTOMEMBERSOFTHEPUBLlCIIW,~~at4.~Qa0~Q+IS0&01.\~K~$~II~IIV~+~oplro&.-lNoIIownVai~>\~~'lII~~IIII~ga~sase~'00SWIe~awl.IIIIIII'auP~\Pl'SUSQUEHANNA STEAMELECTRICSTATIONSITEBOUNDARYDISTANCES (DISTANCES INFEETl~PENNSYLVANIA POWER4UGHTHALUBURTON NUSNavsmber02,.1993LC0%0SvPfILhwnt,koe4pl aeaer%keelaors~Locskn4tor cbeecakuhtiona

.~Laceooooaooooooo73 TABLE25CALCULATED COLLECTIVE DOSESTOMEMBERSOFTHEPUBLICWITHINTHERIVERLANDS/INFORMATION CENTERCOMPLEXDATAPERIOD:1/1/95TO12/31/95EFFL'UENT

.'AGEGROUP-APPLICABLE ORGAN'MAXIMUMDOSERATE"MREM/HRCOL'L'ECTIVE DOSEPERSON-REM NOBLEGASN/ATOTALBODY2.90E-072.90E-05NOBLEGASN/ASKIN7.66E-077.66E-05IODINEANDPARTICULATES TEENLUNG1.95E-061.95E-04Estimated maximumdoserateisbasedonasitetotalactivityrelease.PATHWAYSANALYZED:

PLUME,GROUND,INHALATION Themaximumcalculated dosefromall1995SSESairborneeffluent(bothunits)atthislocationwas1.97E-02mrem(TEEN,LUNG).74 TABLE26CALCULATED DOSESFORRESIDENCES WITHINTHESSESSITEBOUNDARY0.40MILESSESECTORDATAPERIOD:1/1/95TO12/31/95--."-EFFLUENT AGEGROUPAPPLICABLE ORGANESTIMATED, PERCENTMAXIMUMDOSE'OF(MREM)LIMITLIMITMREMNOBLEGASN/ATOTALBODY8.98E-040.02NOBLEGASN/ASKIN2.37E-030.0215IODINEANDPARTICULATES TEENLUNG6.07E-030.041510CFR50,AppendixIlimitsareintermsofmradormrem/reactor-year.

PATHWAYSANALYZED:

PLUME,GROUND,INHALATION Themaximumcalculated dosefromall1995airborneeffluent(bothunits)atthislocationwas1.22E-02mrem(TEEN,LUNG).CALCULATED DOSESFORRESIDENCES WITHINTHESSESSITEBOUNDARY1.10MILESWSWSECTORDATAPERIOD:1/1/95TO12/31/95EFFLUENTAGEGROUPAPPLICABLE ORGANESTIMATED PERCENTMAXIMUMDOSEOF(MREM)LIMITLIMITMREMNOBLEGASN/ATOTALBODY4.69E-030.09NOBLEGASN/ASKIN1.24E-020.0815IODINEANDPARTICULATES CHILDLUNG4.86E-020.321510CFR50,AppendixIlimitsareintermsofmradormrem/reactor-year.

PATHWAYSANALYZED:

PLUME,GROUND,VEGETATION, INHALATION tThemaximumcalculated dosefromall1995SSESairborneeffluent(bothunits)atthislocationwas1.27E-01mrem(CHILD,LUNG).75 TABLE27CALCULATED DOSESFORNEARESTDAIRYFACILITY2.00MILESWSWSECTORDATAPERIOD'/1/95 TO12/31/95:";:;EFFLUENT AGE'PPLICABLE

'GROUP.ORGANESTIMATED MAXIMUMDOSEmremPERCENTOFLIMITLIMITmremNobleGasN/ATotalBod2.06E-030.04NobleGasIodineandParticulates N/AChildSkinLung5.44E-033.64E-020.040.2415'1510CFR50,AppendixIlimitsareintermsofmradormrem/reactor-year.

PATHWAYSANALYZED:

PLUME,GROUND,INHALATION, VEGETATION ANDCOWMILKINGESTION Themaximumcalculated dosefromall1995airborneeffluent(bothunits)atthislocationwas7.26E-02mrem(CHILD,LUNG).76 SECTION5CHANGESTOTHEOFFSITEDOSECALCULATIONMANUALANDTHESOLIDMfASTEPROCESSCONTROLPROGRAM77 CHANGESTOTHEOFFSITEDOSECALCULATION MANUALTheSSESODCMwasrevisedfourtimesin1995.Thechangesin1995aredesignated Revisions 2through5bySSESDocumentControlCenter.InRevision2,Section10.3(Evaluation andMonitoring CriteriaforEffluentPathways) wasexpandedtoshowspecificplantsystemsevaluated inthecategories NOTANEFFLUENTPATHWAY(listedinnewTable8),andINSIGNIFICANT EFFLUENT~PATHWAY(listedinnewTable9).References forthebasesfortheseevaluations areincludedforeachsystemintheTable.Unlessotherwise listed,mostofthesystemswereevaluated inPPRLCalculation EC-ENVR-1 008,whichwasperformed inresponsetoNRCOpenItem91-10-01-07.

ThisrevisiontotheODCMwassubmitted inresponsetoNRCOpen,Item 91-10-01-08.ODCMEquations 7,8,17and18wererevisedtoshowtheGammaShielding'Factor (Si:).ThisfactorhasalwaysbeenusedinGASPARcalculations (NRCcodereferenced intheODCM)forwholebodyandskindosefromnoblegaseffluent.

Theequations wererevisedtobeconsistent withtheapplication oftheGASPARcode.TheGammaShielding Factor(=0.7fortheMaximally-Exposed MemberofthePublic)istakenfromReg.Guide1.109TableE-15.Sections8.1and8.3wererevisedtoreflectthecurrentstateofliquidandsolidradwasteprocessing, respectively.

Figures1,3and4havealsobeenupdatedtoshowchangestoliquidandsolidradwasteprocessing systems,including vendorinterfaces, basedoninformation fromEffluents Management.

Revision2wassubmitted toSSESPORC(1/19/95)andapproved(1/20/95).

InRevision3,Table6(Operational Environmental Monitoring Program)wascorrected toshowinformation originally inRevision1oftheODCM(approved 10/14/94).

Someinformation inthistablewasnotedtobeincorrectly carriedintoRevision2.Table6wasnotintendedtobechangedinanywayinRevision2.Thisinformation wasdocumented asastatuscontrolissueinSOOR95-045;corrections weremadeinresolution tothatSOOR.SlightchangesweremadetoFigure1,LiquidRadwasteSystemFlowDiagram.Thesechangesmadethepathwayfromthedistillate sampletanktothecoolingtowerblowdownpipeclearer,andtocorrectlabelingofdistillate sampletankpumpsOP-327A,BandLRWSampleTankpumpsOP-305A,BandC.InSection10.9.c.2, reference 10CFR20.302 ischangedto10CFR20.2002 tobeconsistent withtherevisioninthenumbering ofthisregulation.

78 140 Systemclassifications andreferences areaddedtoTable8(NOTANEFFLUENTPATHWAY)andTable9(INSIGNIFICANT EFFLUENTPATHWAY).

Table10(SIGNIFICANT EFFLUENTPATHWAY)isaddedwithreferences.

Section11isrevisedtostatethatODCMrevisions shallbereviewedbyPORCafterapprovalbytheManager-NuclearTechnology..

Revision3wassubmitted toSSESPORC(3/30/95) andapproved(3/30/95).

InRevision4,threemilksamplingstations(10G1,10D1and10D2)wereinadvertently deletedinRevision3Table6.Thesedeletions werenotnotedinRevision3Table6,whichwassubmitted inresolution toSOOR95-045.Thenameoftherestaurant atTLDstation6A4wasdeletedtomakethedescription moregeneric(toallowforownership change)inresponsetoaPORCcommentfromthemeetingonMarch30,1995.Revision4wasapprovedbytheManger-NuclearTechnology (4/17/95) andreviewedbySSESPORC(4/20/95).

InRevision5,theintroduction waschangedtospecifythatreference toMPClimitsin10CFR20AppendixBapplytothoselimitsineffectpriortoJanuary1,1994,andcontinuing ineffectuntilsuchtimethatrevised10CFR20AppendixBlimitsareimplemented atSSES.Adescription ofsystemswithNRCI/EBulletin80-10applicability wasaddedtoSection10.3.Reference wasmadetoTable11,whichliststhe80-10systemsbynumberandname.Table9wasrevisedtoincludeRefuelWaterStorageTankwithCondensate StorageTankandBerm,andH>SealOilwithMainTurbine/RFPT LubeOil.TheSewageTreatment PlantwasaddedtoTable9.Reference notesforthesechangeswerelocatedintheappropriate tables.Table11(SystemswithNRCI/EBulletinApplicability) wasaddedtotheODCM.TheSewageTreatment PlantwasaddedtoTable11inresponsetoPORCMeeting95-098ActionItemE05532.Section11(ODCMReviewandRevisionControl)wasrepaginated tofollowTables8-11ofSection10.Reference torevisioninaccordance withNEPM-QA-1011 wasadded,whichwassubmitted asanActiontoPreventRecurrence inSOOR95-045.Thedistribution ofODCMcopieswasrevisedtoindicateSSESDocumentControlServices, whichreplacedthestaffoftheNuclearDepartment Library.79 Revision5wasapprovedbytheManger-NuclearTechnology (7/17/95) andreviewedbySSESPORC(7/20/95).

Consistent withtherequirements ofTechnical Specification 6.14.2.2, therevisedmethodology andparameters donotreducetheaccuracyorreliability ofdosecalculations orsetpointdeterminations.

CopiesofRevisions 2,3,4,and5oftheSSESODCMareincludedunderseparatecoverinAppendixA.80 CHANGESTOTHESOLIDWASTEPROCESSCONTROLPROGRAMTheSSESSolidRadioactive WasteProcessControlProgram,NDAP-QA-0646, wasreviewedandfoundacceptable bythePORC(PORCMeeting95-041)duringthereportpel'Iod.Revision4toNDAP-QA-0646 incorporated PCAF1-94-1330revisingthePCPimplementing procedure matrixtoreflectactualprocedures inuse,andchangedtherequirements fordisposalofradioactive wastesamplesafterpackagedradioactive wastehasbeeninitsdesignated storagearea.PCAF1-94-1330wasincorporated intoNDAP-QA-0646.

ThisPCAFwasimplemented duetotheunavailability ofoffsitedisposalfacilities.

Areviewofexistingregulatory guidanceandimplementing procedures revealsnorequirement tostoreradioactive wastesamplesafterthepackagedradioactive wasteisplacedintoitsdesignated storagearea.Existingrecordsprovidereasonable assurance thatthewastehasbeenproperlyanalyzed.

TheProcedure Matrix(Attachment D)hasbeenrevisedtoreflectchangesintheprocedures.

Pages11,31,57and59wereaffectedbythisPCAF.Thesechangesdidnotreducetheoverallconformance ofthesolidified waste'product toexistingcriteria.

AcopyofSSESRadioactive WasteProcessControlProgram,NDAP-QA-0646, Revision4,isincludedunderseparatecoverasAppendixB.AddedSEGNRC-approved TopicalReportSTD-P-05-001-P-A toContracted VendorServicestoreflectuseofSEGforwasteprocessing equipment, methodsandverification ofacceptable wasteformsfordewatering andsolidification.

Added-Activated Carbonasanewwastetypewhichisgenerated fromprocessing ofliquidwastesusingvendor-provided demineralization services.

AddedtheSolidification/Dewatering/Services Vendormayperformtestsolidification anddetermination ofmixingratiosforsolidification performed offsite(vendorfacility).

AddedRadlok(SEG)-type containers toHighIntegrity Container approvedforuselist.AddedSNMinventory requirements duringprocessing perSOOR94-581resolution.

AddedNRCTechnical PositiononConcentration Averaging andEncapsulation toRadioactive WasteAnalysisandClassification toensurethatradionuclide/

concentrations areadequately distributed overthevolumeorweightofthewaste.81

SECTION6REPORTSOFEXCEPTION TOTHESSESEFFLUENTMONITORING PROGRAM82 I

REPORTSOFEXCEPTION TOTHESSESEFFLUENTMONITORING PROGRAMNooccurrences wereindicated in1995whereaninstrument wasINOPERABLE foradurationsubjecttothereporting conditions ofTechnical Specifications 3.3.7.10b or3.3.7.11.b.

83 SECTION7CORRECTION TODOSESREPORTEDINPREVIOUSSEMIANNUAL ORANNUALEFFLUENTANDWASTEDISPOSALREPORT84 CORRECTIONS TODOSESREPORTEDINPREVIOUSSEMIANNUAL ORANNUALEFFLUENTANDWASTEDISPOSALREPORTSDuringthepreparation ofcalculations todetermine thenuclearfuelcycle(40CFR190) dosetothepubliccontribution fromaproposedindependent spentfuelstorage.installation (ISFSI)atSSES,it.wasnotedthattheprogramGASPARrejectedAg-110mintheairbornesourceterm.Ag-110mwasreportedinairbornesamplesfromSSESonlyin1985,however,itdoesenterthedatabaseforeffluentcalculations fortheISFSIlicensing basis.Thisdiscrepancy causedaCondition Report(CR-95-0743) tobeissued.Duringtheinvestigation ofthisCondition Report,itwasnotedthatAg-110mwasreportedinTable3oftheSSESSemiannual EffluentandWasteDisposalReportsfor1985.Theisotopewasgrieved,however,intheGASPARcalculation submitted forthatperiod,anditwasnotincludedinthedetermination ofdosetoMembersofthePublicreportedatthattime(February 1986).Aseparategaseousdosecalculation hasbeenperformed fortheAg-110mreleasedin1985,usingthedosecalculation factorsintheSSESODCM,andtheactualdispersion (XIQ,D/Q)estimates fortheoffsitereceivers reportedfortheperiod.Table28showsthemaximumdosesforthereleaseof148pCiAg-110min1985,calculated bymaximumagegroupandorganforeachoffourreceiverlocations:

TABLE28AIRBORNEEFFLUENTOFFSITEDOSEFROMAg-110m:1985LOCATIONPATHWAYSAGEGROUPORGANDOSEmrem0.7milesWSWSiteBounda1.7milesWSWDaiAnimal1.2milesWSWGarden1,61,2,3,5,61,5,6TeenTeenTeenLunG.I.G.l.8.75E-046.04E-043.98E-041.2milesWSWResident1,2,3,4,5,6 TeenG.l.1.17E-03wherepathway1=groundshine2=goatmilkingestion 3=cowmilkingestion 4=meatingestion 5=vegetable ingestion 6=inhalation Thehighestdosecalculated (1.17E-03mrem)fromAg-110misapproximately 1%ofthatreportedforMembersofthePublicduetoallotherairborneiodineandparticulate

.effluentin1985.85 SECTIONSEFFLUENTFROMADDITIONAL MONITORED RELEASEPOINTS86

EFFLUENTFROMADDITIONAL MONITORED RELEASEPOINTSThetemporary laundryfacilityisaprocessing systemlocatedinatraileratthenorthendoftheplant,neartheradwastebuilding.

Sincethefacilityprocesses contaminated laundry,thetraileratmosphere issampledroutinely forairborneactivity.

Theeffluentpotential forthissystemwasdetermined inSafetyEvaluation NL-90-029.

Ithasbeenclassified asanInsignificant EffluentPathwayintheODCM.Thefacilityhasbeenincontinuous usesince1991.Airborneeffluent.

sampleshavebeentakensinceoperations began,withresultstypically indicating belowdetection level.In1995,severalairsamplestakenfromthetrailerwerenotedtohaveMn-54abovetheminimumdetectable activity.

Thefollowing airborneparticulate effluentandresulting offsitedosetomembersofthepublicattheresidence 1.1milesWSWisreportedforthetemporary laundryfacility.

Thiseffluentandresulting offsitedoseisreportedsupplementary toTables3,4,24and26sinceitisminorrelativetothequantities reportedtherein(i.e.notobservable atthreesignificant figures):

TABLE29AIRBORNEPARTICULATE EFFLUENTFROMLAUNDRYTRAILERIsotoeEffluentReleasedCiMn-546.54E-08TABLE30OFFSITEDOSE(RESIDENCE AT1.1MILESWSW)RESULTING FROMLAUNDRYTRAILEREFFLUENT'EFFLUENT

'GEGROUPAPPLICABLE ORGANESTIMATED MAXIMUMDOSEMREMLIMITMREM'PERCENT",OFL'IMIT"-'.Particulate TeenLun9.51E-08156.34E-0787 APPENDIXAREVISIONS TOSSESODCM

PENNSYLVANIA POWER5LIGHTCOMPANYSUSQUEHANNA STEAMELECTRICSTATIONOFFSITEDOSECALCULATION MANUALRevision2PreparedByDateReviewedBySupervisor-Environmen alServicesNucearReviewedByingo.ApprovedBy4.AManager-Nuclear Technology Date//OateDate SUMMARYOFODCNCHANGESChangesotherthanthoseofaminor,editorial naturearesummarized below.1.Section10.3(Evaluation andMonitoring CriteriaforEffluentPathways) hasbeenexpandedtoshowspecificplantsystemsevaluated inthecategories NOTANEFFLUENTPATHWAY(listedinnewTable8),andINSIGNIFICANT EFFLUENTPATHWAY(listedinnewTable9).References forthebasesfortheseevaluations areincludedforeachsystemintheTable.Unlessotherwise listed,mostofthesystemswereevaluated inPP8LCalculation EC-ENVR-1008, whichwasperformed inresponsetoNRCOpenItem91-10-01-07.

ThisrevisiontotheODCMissubmitted inresponsetoNRCOpenItem91-10-01-08.

2.Equations 7,8,17and18arerevisedtoshowtheGammaShielding Factor(Sq).ThisfactorhasalwaysbeenusedinGASPARcalculations (NRCcodereferenced intheODCM)forwholebodyandskindosefromnoblegaseffluent:

theequations arerevisedtobeconsistent withtheapplication oftheGASPARcode.TheGammaShielding Factor(0.7for'heMaximally-Exposed Memberofthe.Public)istakenfromReg.Guide1.109TableE-15.3.'ections8.1and8.3havebeenrevisedtoreflectthecurrentstateofliquidandsol,idradwasteprocessing, respectively.

Figures1,3and4havealsobeenupdatedtoshowchangestoliquidandsolidradwasteprocessing systems,including vendorinterfaces, basedoninformation fromEffluents Management.

Rev.2 TABLEOFCONTENTSAPPROVALPAGEDATEREVISIONDATE

1.0INTRODUCTION

.

2.0SETPOINTS...............................

~.2.1WATERBORNE EFFLUENTMONITORS..........

2.2AIRBORNEEFFLUENTMONITORS............

3.0 WATERBORNE

EFFLUENTCONCENTRATION MEASUREM4.0AIRBORNEEFFLUENTDOSERATES.............

4.1NOBLEGASES.......

4.2RADIONUCLIDES OTHERTHANNOBLEGASES..5.0INDIVIDUAL DOSEDUETOWATERBORNE EFFLUENT5.1FISHPATHWAYLIQUIDEFFLUENTDOSECALCULATION METHODOLOGY....

5.2POTABLEWATERPATHWAYEFFLUENTDOSECALCULATION METHODOLOGY...............

5.3SHORELINE EXPOSUREPATHWAY.,5.4PROJECTED DOSEFROMLIQUIDEFFLUENT...

I6.0INDIVIDUAL DOSEDUETOAIRBORNEEFFLUENT..

6.1NOBLEGASES........

6.2RADIONUCLIDES OTHERTHANNOBLEGASES..7.0TOTALDOSE8.0OPERABILITY OFWASTETREATMENT SYSTEMS....

8.1LIQUIDWASTETREATMENT................

8.2GASEOUSWASTETREATMENT.

8.3SOLIDWASTETREATMENT

.......,.........

~t~~~~~~~~~~ENTS~~~~~~~~~~~~~~~~~~~~~~~~~~~~~1~~~~~~~~~~~~~~~~~~~~~2345678910111213141515161718192021222324242526272728293031323233'34363710/29/932/5/9211/9/93'/5/92 2/5/9212/11/892/5/9212/11/8912/11/892/5/9212/11/8912/11/8911/21/922/5/922/5/922/5/921/16/951/16/952/11/922/5/9212/11/8912/1/9210/29/933/11/942/21/923/ll/942/21/922/21/92'12/11/89 2/21/9212/11/8912/11/892/21/9212/11/8912/11/8911/25/922/21/922/21/922/21/921/20/951/20/952/21/92~2/21/9212/11/8912/4/923/11/94ll/9/93ll/9/93ll/9/932/18/94ll/9/9310/29/9310/29/9310/29/9310/29/931/16/9510/29/9310/29/931/16/951/16/951/16/951/16/951/16/951/16/953/11/943/11/943/ll/943/11/943/ll/943/ll/943/11/943/11/943/ll'/941/20/953/ll/943/ll/941/20/951/20/951/20/951/20/951/20/951/20/952/18/943/11/94DATPev.2 aE APPROVALREVISIONPAGEDATEDATE9.0RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM.9.1DEFINITIONS...............................

9.2MONITORING PROGRAM...

9.3CENSUSPROGRAM...............'.............

9.4INTERLABORATORY COMPARISON PROGRAM........

4242424344451/16/951/16/951/16/951/16/951/16/951/16/951/20/951/20/951/20/951/20/951/20/951/20/9510.0DOSE10.110.210.310.410.510.610.710.810.9ASSESSMENT POLICYSTATEMENTS............

SELECTION OFANALYSISRESULTSFORDOSECALCULATIONS ASSIGNMENT OFRELEASESTOTHEREACTORUNITSEVALUATION ANDMONITORING CRITERIAFOREFFLUENTPATHWAYSFLOWFROMTHESGTSVENTWHENTHESYSTEMISNOTINUSEODCHSETPOINTS AREUPPERLIHITVALUESDEFINITION OF"APPROPRIATE TREATMENT" FORLIQUIDWASTESHONITORLINE-LOSS CORRECTIONS SELECTION OFDATAFORDETERMINATION OFDOSERATECOMPLIANCE LOW-LEVEL RADIOACTIVITY INTHESEWAGETREATMENT PLANT535353535455555757581/16/951/16/951/20/951/20/951/16/951/16/951/16/951/16/951/20/951/20/951/20/951/20/951/16/951/20/951/16/951/20/951/16/951/20/951/16/951/20/9511.0ODCHREVIEWANDREVISIONCONTROL.............

APPENDIXA-SAMPLECALCULATIONS OFODCMPARAMETERS...........................

IAPPENDIXB-REPORTING REQUIREMENTS...............

60A-1A-2A-3A-4A-5A-6A-7A-8A-9A-10A-11A-12A-13B-lB-2B-38-41/16/952/5/922/5/9212/11/892/5/9210/29/9310/29/9310/29/9310/29/932/5/922/5/9210/29/9310/29/9310/29/9312/11/8910/29/9312/11/8912/11/891/20/952/21/922/21/9212/11/892/21/923/ll/943/ll/943/ll/943/ll/942/21/922/21/923/ll/943/ll/943/ll/9412/11/893/ll/9412/11/8912/11/89DATRev.2

~'V' PAGEAPPROVALDATEREVISIONDATE5-6cComposite DoseFactors:HaximumHypothetical Child(2pp)....................................5-6c(1,2) 2/18/945-6dWaterIngestion DoseFactors:HaximumHypothetical Infant(2pp)......................5-6d(1,2) 2/18/943/ll/943/ll/946Operational Radiological Environmental Honitoring Program..

.....................

4849501/16/951/16/951/16/951/20/951/20/951/20/957Detection Capabilities forEnvironmental SampleAnalysis................

.............

51528SystemsClassified asNotanEffluentPathway...

611/16/951/20/951/16/951/20/951/16/951/20/959SystemsClassified asInsigni'ficant Effluentpathwayo~~~~~~~~0~~~~~~~~~~~~~~~~~~~~~~621/16/951/20/95D-1DilutionFactorsandTransitTimesforSSESEffluents toOanville, PA...........

.D-1B-lRadiological Environmental Honitoring ProgramAnnualSummary..............................

8-3B-2Reporting LevelsforNonroutine Operating eportso~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~tB4R12/11/89ll/9/933/ll/943/ll/9412/11/8912/11/89 LISTOFFIGURESAPPROVALREVISIONPAGEDATEDATEFigure2OffgasandRecombiner SystemF'towDiagram........

~~~~~~o39Figure3SolidWasteManagement SystemFlowOiagram..........................

40Figure4SSESDryContaminated WasteProcessing............................

41Figure5Environmental Monitoring Locations WithinOneMileofSSES...'............

46Figure6Environmental Monitoring Locations GreaterthanOneMilefromSSES.......

47Figure1LiquidRadwasteSystemFlowDiagram.......................:..

381/16/951/20/951/16/951/20/951/16/951/20/951/16/951/20/951/16/951/20/951/16/95'/20/95DATRev.2vi

4.0 AIRBORNEEFFLUENTDOSERATESSPECIFICATION

3.11.2.1.

THEDOSERATEDUETORADIOACTIVE MATERIALS RELEASEDINGASEOUSEFFLUENTS FROMTHESITE(SEEFIGURE5.1.3-1)SHALLBELIMITEDTOTHEFOLLOWING:

a.FORNOBLEGASES:LESSTHANOREQUALTO500MREM/YRTOTHETOTALBODYANDLESSTHANOREQUALTO3000MREM/YRTOTHESKIN,ANDb.FORIODINE-131, FORTRITIUM,ANDFORALLRADIONUCLIDES INPARTICULATE FORMWITHHALF-LIVES GREATERTHAN8DAYS:LESSTHANOREQUALTO1500MREM/YRTOANYORGAN(INHALATION PATHWAYONLY).4.1~IIOBiAEEKNoblegasactivitymonitorsetpoints areestablished atreleaserateswhichpermitsomemarginforcorrective actiontobetakenbeforeexceeding offsitedoseratescorresponding tothe10CFR20annualdoselimitsasdescribed inSection2.2.Themethodsforsamplingandanalysisofcontinuous ventilation

.releases aregivenintheapplicable plantprocedures.

Thedoserateinunrestricted areasduetoradioactive materials releasedinairborneeffluents maybedetermined bythefollowing equationforwholebodydose:Z(Ki(X/Q)v (Q')v)(Sp) 1andbythefollowing equationforskindose:Dg[L.+((1.11(Mi)(S~))]

(X/Q)(Q'))

~1(Eq.7)(Eq8)DAT'Rev.215 NJ 4.0AIRBORNEEFFLUNTDOSERATESSPCIFCATION3.1.2.1.THEDOSERATEDUETORADIOACTIVE MATERIALS RELEASEDINGASEOUSEFFLUENTS FROMTHESITE(SEEFIGURE5.1.3-1)SHALLBELIMITEDTOTHEFOLLOWING:

a~b.FORNOBLEGASES:LESSTHANOREQUALTO500MREM/YRTOTHETOTALBODYANDLESSTHANOREQUALTO3000MREM/YRTOTHESKIN,ANDFORIODINE-131, FORTRITIUM,ANDFORALLRADIONUCLIDES INPARTICULATE FORMWITHHALF-LIVES GREATERTHAN8DAYS:LESSTHANOREQUALTO1500MREM/YRTOANYORGAN(INHALATION PATHWAYONLY).0'4.1N~OBaASNoblegasactivitymonitorsetpoints areestablished atreleaserateswhichpermitsomemarginforcorrective actiontobetakenbeforeexceeding offsitedoseratescorresponding tothe10CFR20,annualdoselimitsasdescribed inSection2.2.Themethodsforsamplingandanalysisofcontinuous ventilation releasesaregi'venintheapplicable plantprocedures.

Thedoserateinunrestricted areasduetoradioactive materials releasedinairborneeffluents maybedetermined bythe,following equationforwholebodydose:Z()(/0)y(0'fy)(p)1andbythefollowing equationforskindose:Dg[L+((1.11(Mi)(Sr))j(X/9)v(9'iv)~1(Eq7)(Eq8)DAT'Rev.215" where:K.thewhole-body dosefactorduetogammaemissions foreachiden)ified noblegasradionuclide (i)(mrem/yrperuCi/m)fromTable2.thereleaserateofradionuclide (i)fromvent(v)(uCi/sec).

(X/g)thehighestcalculated annualaveragerelativeconcentration foranyareaatorbeyondthesiteboundaryinanu~restricted areafromventreleasepoint(v)(sec/m)suchasfromTable3.wbLitheannualwhole-body dose(mrem/yr).

theskindosefactorduetothebetaemissions foreachiden)ified noblegasradionuclide (i)(mrem/yrperuCi/m)fromTable2.theairdosefactorduetogammaemissions foreachidentjfied noblegasradionuclide (i)(mrad/yrper'Ci/m)fromTable2(conversion constantof1.1convertsairdose-mrad toskindose-mrem).

Dtheannualskindose(mrem/yr).

sS,thegammashielding factor(0.7formaximally exposedindividual)

Samplecalculations fordetermining wholebodyandskindosesfromnoblegasradionuclides releasedfromtheSSESaregiveninSectionA.2.1ofAppendixA.'4.2RADIONUCLIDES OTHERTHANNOBEGASESThemethodsforsamplingandanalysisofcontinuous ventilation releasesforradioiodines andradioactive particulates aregivenintheapplicable plantprocedures.

Additional monthlyandquarterly analysesshallbeperformed inaccordance withTable4.11.2.1.2-1 oftheSSESTechnical Specifications.

Thedoserateinunrestricted Iareasduetoinhalation ofradioactive materials releasedinOATRev.216

7.0OT0C03.-THEANNUAL'(CALENDAR YEAR)DOSEORDOSECOMMITMENT TOANYMEMBEROFTHEPUBLIC,DUETORELEASESOFRADIOACTIVITY ANDRADIATION, FROMURANIUMFUELCYCLESOURCESSHALLBELIMITEDTOLESSTHANOREQUALTO25MREMSTOTHETOTALBODYORANYORGANEXCEPTTHETHYROID,WHICHSHALLBELIMITEDTOLESS.THANOREQUALTO75MREMS.Thecumulative dosetoanymemberofthepublicduetoradioactive releasesfromtheSSESsiteisdetermined bysumaingthecalculated dosestocriticalorgansfromthepreviously discussed effluentsources.Theannualdosetocriticalorgansofamaximally exposedindividual fortheliquideffluents isdetermined byusingEquations 10,ll,and12ofSection5..Theannualdosetocriticalorgansofarealindividual forthenoblegasesreleasedinthegaseouseffluents isdetermined by.usingEquation14modifiedbyreplacing M.withK.fromTable2forthewhole-1ibodydoseandbyEquation15modifiedbyreplacing Niby[Li+((1.11 Mi)(S,))]

fromTable2fortheskindoseofSection6.0:1D317x10Ki(X/g)v(g)y)(Sp)

(Eq.17)Db3.17x10fL.+((l.llM.)(S,))](X/g)(g',.)

(Eq.18)Theannualdosetocriticalorgansofarealindividual fortheradionuclides otherthannoblegasesreleasedinthegaseouseffluents isdetermined byusingEquation16ofSection6.0.Foralldosecalculations fromairborneeffluents, thedeposition rateusedintheanalysisshouldbeatthereceptorlocationoftheindividual beingevaluated, notthehighestcalculated annualaveragerelativeconcentration orrelativedeposition rateforanyareaatorbeyondthesiteboundaryasgiveninTable3.Thedirectradiation fromthesiteshouldbedetermined fromtheenvironmental monitoring program's directradiation (TLD)monitors.

Sinceallotheruraniumfuelcyclesourcesaregreaterthan20milesaway,onlytheSSESsiteneedbeconsidered asauraniumfuelcyclesourceformeetingtheEPAregulations.

Inactualpractice, theLADTAPandGASPARcomputercodedeveloped bytheNRCtoimplement theliquidandgaseousdosemethodology ofRegulatory Guide1.109willbeusedtoperformthetotaldose.calculations fortheIDATRev.230 1

8.0PTYFWATATTSYSTMASTSPCIFCATION3.11..3-THELIQUIDRADWASTETREATMENT SYSTEM,ASDESCRIBED INTHEODCM,SHALLBEOPERABLE.

THEAPPROPRIATE PORTIONSOFTHESYSTEMSHALLBEUSEDTOREDUCETHERADIOACTIVE MATERIALS INLIQUIDWASTEPRIORTOTHEIRDISCHARGE WHENTHEPROJECTED DOSESDUETOTHELIQUIDEFFLUENT, FROMEACHREACTORUNIT,TOUNRESTRICTED AREA(SEEFIGURE5.1.3-1)WOULDEXCEED0.06MREMTOTHETOTALBODYOR0.2MREMTOANYORGANINA31-DAYPERIOD.TheSSESLiquidRadWasteManagement systemconsistsofthreeprocessing sub-systems, liquid,chemicalandlaundry.Redundant andbackupequipment, alternate processroutes,interconnections andsparevolumesaredesignedintothesystemtoprovideforoperational andunanticipated surgewastevolumesduetorefueling, abnormalleakagerates,decontamination activities andequipment'owntime, maintenance andrepair.TheLiquidRadWasteManagement Systemprocesses equipment drainandfloordrainliquidscollected inacommonplantdrainagesystem.Thesystemalsoprocesses filterbackwash, resintransferliquidsandresincleaningliquids.Thesystemhaspipingconnections toallowtheinstallation ofvendor-supplied equipment toprovidespecifictreatment ofoff-normal wastesortoenhancethenormaltreatment capabilities asnecessary.

Appropriate vendor-supplied equipment mayalsobeusedinplaceofinstalled equipm'ent toallowfor'epair orreplacement ofcomponents.

Lowconductivity liquidwastesareprocessed intheLiquidRadwasteTreatment Sub-system.

Liquidiscollected inthreepairsofLRWCollection tanks.Eachpairoftankshasanapproximate capacityof28,000gallons.Surgecapacityismaintained withtwopairsLRWSurgeTanksalsowitha28,000gallon/pair capacity.

DATLiquidsfromthesetanksarenormallyprocessed throughtwoverticalcentrifugal discharge precoatfilterswith300ftfilterareaata200gpmnormalflowrate.Liquidfromthefiltersisthensenttoamixedbeddemineralizer withavolumeof140ftandnormal.flowrateof200gpm.Thedemineralizer effluentiscollected inthreepairsofLRWSampleTanks.Each32Rev.2 pairoftankshasan'pproximate capacityof28,100gallons.ThewaterisisolatedinthesetanksforanalysispriortorecycletoUnit1ordischarge totheSusquehanna river.Off-specification liquidscanberecycledbacktotheLiquidRadWasteManagement System,foradditional processing.

Highconductivity wastesarecollected intheChemicalDrainTankandinspecificsumpslocatedintheTurbineandRadwasteBuildings.

Liquidfromthesesourcesiscollected inaChemical,'WasteTankofapproximately 12,000gallonscapacity.

ThisliquidcanthenbesenttoanyoneoftwopairsofChemicalWasteNeutralizing Tanks.Eachpairhasacapacityof31,000gallons.Theliquidisthensenttoavendor-supplied ChemicalWasteProcessing Sub-system forradionuclide removal.TheeffluentfromtheChemicalWasteProcessing Sub-system isroutedtotheEvaporator Distillate SampleTankwhereitcanbeisolatedforanalysispriortodischarge.

Thecapability existstoreturntheliquidtotheLiquidRadWasteManagement Systemforadditional processing ifnecessary.

TheLaundryWasteSub-system collectswaterfromwashdown, laundryanddecontamination facilities inoneoftwoLaundryDrainTanks.Eachtankhasacapacityofapproximately 820gallonsandhasanindependent mechanical filtersystem.Onetankisnormallyvalvedtoreceivewastewhiletheotherisvalvedforprocessing.

EffluentfromthesetanksisroutedtotheLaundryDrainSampleTankwhereitcanbeisolatedforanalysispriortodischarge.

Non-specification liquidcanbereturnedtotheChemicalWasteProcessing Sub-system.

AflowdiagramoftheLiquidRadwasteManagement SystemisshowninFigurel.OATAppropriate treatment forliquideffluents fromSSESisdefinedinODCNPolicyStatement 10.6;Incaseswhenabatchofliquidwastemustbereleasedwithtreatment lessthanthatspecified inSection10.6,adoseassessment usingLADTAPorthemethodology 33Rev.2" ofSection5.4shallbeperformed priortoreleasetoensurethatthelimitsofSpecification 3.11.1.3arenotexceeded.

8.2GASOUSSTATMENTSPECIFICATION 3.11.2.4-THEGASEOUSRADWASTETREATMENT SYSTEMSHALLBEINOPERATION.

~PPCAE'IIIENEYER TIIIMAINCIINRENEER AIRECECTIIRTETACYATIIINT SYSTEMISINOPERATION.

SPECFICON3.1.2.5-THEAPPROPRIATE PORTIONSOFTHEVENTILATION EXHAUSTTREATMENT SYSTEMSHALLBEOPERABLEANDSHALLBEUSEDTOREDUCERADIOACTIVE MATERIALS INGASEOUSWASTEPRIORTOTHEIRDISCHARGE WHENTHEPROJECTED DOSESDUETOGASEOUSEFFLUENTRELEASESFROMEACHREACTORUNITTOAREASATANDBEYONDTHESITEBOUNDARY(SEE,FIGURE5.1.3-1)WHENAVERAGEDOVER31DAYSWOULDEXCEED0.3MREMTOANYORGANINA31-DAY'ERIOD.

TheSSESoffgastreatment systemoperateswithfoursteamjetai'rejectorsmaintaining cond'enser vacuum.Noncondensible gasesarepassedthroughoneofthreerecombiners (oneforeachreactorunitplusacommonrecombiner),

reducingtheamountofgasestobefilteredandreleased.

Gasespassthroughatwotonineminuteholduppipebeforeenteringtheoffgastreatment system,whichconsistsofone100percentcapacitysystemperreactorunit.Eachsystemconsistsofprecoolers,

chillers, reheaters, guardbeds,andfivecharcoalabsorbers andanoutletHEPAfilter.Monitored, filteredairthenexitstotheturbinebuildingvent.Aflowdiagramoftheoffgasandrecombiner systemisshowninFigure2.IOATFilteredexhaustsystemsserveselectedareasofZoneI,II,andIIIoftheSSESreactorbuilding.

TheZoneIandZoneIIequipment compartment andZoneIIIfilteredexhaustsystemseachconsistoftwo100'apacity redundant fansandtwo55Xcapacityfiltertrains.Eachfiltertrainhas,inthedirection ofairflow,roughingfilters,upstreamHEPAfilters,acharcoalfilterbed,anddownstream HEPAfilters.Exhaustfandischarge isthenroutedtotheatmosphere viathereactorbuildingvents,whereeffluents arecontinuously sampledandmonitored.

\Rev.2

Theturbinebuildingfilteredexhaustsystemdrawsairfromthoseareasofthebuildingthataremostlikelytobecomecontaminated.

Two100Xcapacityfansserveeachsystem,whichcontainstwo50Xcapacityfilterhousingsmadeupofaparticulate prefilter, anupstreamHEPAfilter,acharcoalfilter,andadownstream HEPAfilter.Discharged airisreleasedviatheturbinebuildingvents,whicharecontinuously sampledandmonitored.

Theradwastebuildingfilteredexhaustsystemdrawspotentially contaminated airfromselectedareasoftheradwastebuilding.

Thesystemcontainstwo100Xcapacityfansandtwo50Xcapacityfilterhousings, eachcontaining aparticulate filterbankandaHEPAfilter.Filteredairisdischarged viatheturbinebuildingvent.Inordertominimizethequantities ofradioactivity inairborneeffluents fromthestation,theventilation exhausttreatment (filtered exhaust)systemsarenormallykeptinserviceatSSES.Astheneedarises,thesesystemsareperiodically renderedinoperable formaintenance'or testingactivities.

Ifthemostrecent31-daydoseprojection indicates thatdosemayexceed0.3mRemtoanyorganwhenaveragedovertheprojected 31-dayperiod,treatment systemsrenderedinoperable willberestoredtooperablestatusasquicklyasispracticable.

Thedoseprojections areperformed atleastonceper31daysbasedonthemostrecentlyavailable effluentdata.Ifitisknownpriortoperforming thedoseprojection thatatreatment systemwillbeoutofservice,and.ifdataexistswhichindicates howthelackoftreatment willimpacteffluents, thesefactorswillbeconsidered whenperforming thedoseprojection.

At'rVDATRev.235 8.3SOIWASTTTNTP0-THESOLIDRADWASTESYSTEMSHALLBEUSEDINACCORDANCE WITHAPROCESSCONTROLPROGRAM,FORTHEPROCESSING ANDPACKAGING OFRADIOACTIVE WASTESTOENSUREMEETINGTHEREQUIREMENTS OF10CFRPART20,10CFRPART71,ANDFEDERALREGULATIONS COVERINGTHEDISPOSALOFTHEWASTE.TheSSESsolidradwastesystemcollectsallwetwastesproducedfromtheoperation ofotherplantsystems.Thewastesarethenprocessed andpackagedbyavendor-supplied systemintoawasteform'hatmeetsallapplicable Federal,Stateandlocalrequirements fortransportation, storageanddisposal.

Theprocessing methodology andacceptance criteriaforthefinalwasteformsarecontrolled bytheProcessControlProgram.FiltermaterialfromtheReactorWaterClean-upSystemsandtheFuelPoolClean-upSystemsarecollected inBackwashReceiving Tanks.ThereisoneRWCUtankperunit,eachwithacapacitypfapproximately 2450gallonsandonesimilartankfortheFPCUSystem.Wastesfromthesetanksaredirectedtooneoftwo6300galloncapacityPhaseSeparators.

Normally, one'hase'Separator isvalvedtocollectwastewhiletheotherisisolatedtoprovidetimeforradioactive decay.Thesolidcontentofthewasteisconcentrated inthePhaseSeparator andtransferred andprocessed throughavendor-supplied systemandpackagedforstorageorfinaldisposal.

Thesupernatant liquidiscollected andprocessed bytheLiquidRadWasteManagement System.TheWasteSludgePhaseSeparator isa9500galloncapacityphaseseparator tankthatacceptsinputfromtheRegenWasteSurgeTanks.Theconcentrated wasteisthentransferred andprocessed throughavendor-supplied systemandpackagedforstorageorfinaldisposal; Thesupernatant liquidiscollected andprocessed bytheLiquidRadWasteManagement System.DATRev.236 SpentbeadresinfromtheCondensate SystemandfromtheLiquidRadwasteDemineralizer

'arecollected intheSpentResinTank.Thesearethenprocessed throughavendor-suppliedsystemandpackagedforstorageorfinaldisposal.

SpentfiltermaterialfromtheLiquidRadwasteFiltersarecollected intwoWasteHixingTanks.Thecontentsofthesetanksare-processed throughavendor-supplied systemandpackagedforstorageorfinaldisposal.

AflowdiagramoftheSSESsolidradwastetreatment systemisshowninFigure3.DryActiveWaste(DAW)consistsofcontaminated plastic,paper,clothing, metalorothertrashandiscollected throughout theRCAofSSES.OAWisprocessed andpackagedforstorageordisposalusingoff-sitevendor-supplied supercompaction andincineration services.

OAWmayalsobecompacted withanon-site'drumcompactor into55-gallon drums.Anautomated DAWmonitoring systemisusedtoensurenon-radiological wastecollected intheRCAisfreefromradiological contamination priortorelease.AflowdiagramofDAWprocessing atSSESisshowninFigure4.Rev.237 EVAP.STEAMCONDS.TANKPHASESEPARATORS (DECANTATE)

RHRSYSTEMRwcuSYSTEMREACTORWELLSEALLEAKDRAINREACTORBLDG.DRAINS+-DRYWELLDRAINSTLSBINEBLDG.DRAINSAADWASTEBLDG.DRAINSLIQUIDRADWASTEFIGURELIQUIDRADWASTESYSTEMFLOWDIAGRAMLIQUIDRADWASTECOLLECTION 8SURGETAHKSOT.302ATHRUFOT.304ATHRUDLIGUIDRADWASTEFILTERSOF-302A,BLIGUIDRADWASTEDENINERALIZEA OF-301LIauIDRADWASTESAMPLETANKSOT-303ATHRUFCONDENSATE DEVIH.RESINAEGHERATIHQ TANKLRWCOLLECTION TANKPNLPSOP-301h>B,CTOWASTEMIXINQTANKSOT-307A,BTOSPENTAESIHTANKOT-324CONDENSATE STORAGETANKSOT-522A,BCHEVIGALWASTEHEUTAALIZEA TANKS1T-130A,B2T~130A,BCSTBEAMWATEASAMPLESTATIONSAUXBOILERBLOWDOWNS RWCUCHEVICALDECON.LABAHDDECOH.DRAINSLAUM)RYDRAINSREGLAATED SHOPDRAINSPERSONALDECONTAM-INATION{OETEAGEHTS)

CASKCLEAHIHGDRAINSCHEMICALWASTETANKOT-314CHEM.WASTENEUTRALIZING TANKPNIPS1P130A>82P-130A,BCHEMWAS'TETANKPWPSOP-328A>8RADWASTEEVAPORATOR OE-302A,BCHEMICALWASTEPAOCESSINQ SUB-SYSTEM (VENDORSUPPLIED)

DISTILLATE SAMPLETANKOT-321EVAPORATOR COHCENTRATE STORAGETANKOT-322LRWSAMPLETANKPLNPSOP-305A>B,CRETOCODLINGTOWERBLOW-DOWNPIPETOWASTEMIXINGTANKSOT-307A>8DATt6LAUNDRYDRAINTANKOT-314A,BRev.2LAUNDRYDAAINTANKPUMPSOP.318A>8LAUHDRYDRAINFILTERSOF-318A>8LAUNDRYDRAINSAMPLETANKOT-312CONCENTRATE BTORAGETANKDISCH.PQIPOP-328LAUNORVDRAINSAMPLETANKPUMPSOP.319A,B OfFGASRFCOMBINERSYSlfMIAMBIENtTEMPFRATURECI<aRCOAI OFFGASSYSTEMUNITIMaINdAUXSIEAMSlfAMJETAIREJECIORUNIIIIURBINESLOGEXIIAUStUNITIIF302OULETHEPAFILTE IIARQALAOSRBEIIBE5FROM>NIIINhlilStfAIICOIIOTIITfhUIIII'il5IAGESTEA>JETA'I5EJEC1011COBDfII.SEIIOIFIIASBYPASSELHEaiIRACINGl-Qr-------)

IDILUTIONSTEAMIIIII2naSTAGA2IIE13hI'RfHEAIEII15125RECOMBVESSELI04-'E131RECOMBCONDIE13iMOTIVESTEAMJET5CONDDELAYPFPEI112IFIA~IEIAIE3A5IT303aINLETPRECIIILIER~ZGUARONEPACOOl.ffiusB0FILTERZit3iait305IT.30Bii301il3aaQCOMMONOFFGASRECOMBINER SYS'EMIIAI1sSTEACOIIDER.SEIIOhlttSIEAMJETAIRfJECTORCONDENSER UNI'T2DELAYPIPEAMBIENTTEMPERATURE CIIAIICOAL OFFGASSYSTfM UNIT2MAIte5AUXStfAUPRODUNIT2OFFGASBYPASSOFFGASRECOMBINER SYSTEM2TURBINEBLOGEXHAUSTUNIT2FIGURE2OFFGASANDRECOHBIHER SYSTEMFLOHDIAGRAMOATRev.2 FIGURE3SOLIDWASTEMANAGEMENT SYSTEMFLOWDIAGRAMCONDENSATE DEMIHRESIHSTORAGEVESSEL1T-159RADWASTEDEMIHERALIZERSTORAGEVESSELOF-301CONDENSATE DEMIHRESINSTORAGEVESSEL2T-158FUELPOOLF/0BACKWASHRECEIVINO TANKOT-203.RWCUBACKWASHRECEIVING TANK1T-225RWCUBACKWASHRECEIVINO TANK2T-225SPENTRESIHTANKOT-324REGEHWASTESUADETANKS1T-108A,BREOENWASTESURGETANKS2T-108A,BSPENTRESINTRANSFERPUMPOP-3201P-108A,BREGEHERATIOH WASTETRANSFERPUMPSITOVENDORLIOUIORAWASTEFILTERSOF-302A>8WASTESLUDGEDISCHARGE IIIXIHGPUMPOP-332TORWSSPUMPWASTESLUDGEPHASESEPARATOR OT-331RWCUPHASESEPARATOR OT-318ARWCUPHASESEPARATOR OT-318BWASTEMIXINGTAHKSOT-307A,BTOVEHDORTORWSSPUMPEVAPORATOR.

CONCENTRATE STORAGETANKDISCHARGE PUMPOP-328EVAPORATOR COHCENTRATE STORAGETANKOT-322RWCUSLUDGEDISCHARGE lllXIHGPUMPOP-3NFROMEVAPORATOR DATRev.2 FIGURE4SSESORYACTIVEWASTE(OAW)PROCESSING Non-radiological TrashfromRCAPaper,Plastic,Rags,ClothingfromRCASecond-Sort DAWDryActiveWaste(DAW)Monitoring SystemPPKLRadioactive?

YesVendorServicesSupercompaction Incineration DrumCompactor 55-gal.DrumsorBoxesNoFreeReleasedzrOATRev.2 9.0RADOGCNVI0NTAMONTORINGPROGRAH~~N.l~NNTIIINNWeekly:Onceineachcalendarweekatintervals ofapproximately 7days,plusorminus2days.Semi-Monthly:

Twiceeachcalendarmonthatintervals ofapproximately 15days,plusorminus4days.Honthly.Onceeachcalendarmonthatintervals ofapproximately 30days,plusorminus6days.quarterly:

Onceineachthreemonthperiodofacalendaryearatintervals ofapproximately 13weeks,plusorminus3weeks.9.2MONITORNGPROGRAHSPCFICTION3.1-THERADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAMSHALLBECONDUCTED ASSPECIFIED INTABLE3.12.1-1.

Environmental samplesshallbecollected andanalyzed(asamini'mum) according toTable6atlocations showninFigures5and6.Analytical techniques usedshallensurethatthedetection capabilities inTable7areachieved.

Adustloadingstudy(RHC-TR-81-01) wasconducted toassurethatthepropertransmission factorwasusedincalculating grossbetaactivityofairparticulate samples.Thisstudyconcluded thatthesamplecollection frequency ofonceperweekwassufficient andthattheuseof1forthetransmission correction factorforgrossbetaanalysisofairparticulate samplesisvalid.Thecharcoalsamplercartridges usedintheairborneradioiodine samplingprogram(ScienceApplications, Inc.,ModelCP-100)aredesignedandtestedbythemanufacturer toassureahighqualityofradioiodine capture.Acertificate fromthemanufacturer issuppliedandretainedwitheachbatchofcartridges certifying thepercentretention ofradioiodine versusairflowratethroughthe'cartridge.

DATRev.242 Theresultsoftheradiological environmental monitoring programareintendedtosupplement theresultsoftheradiological effluentmonitoring byverifyingthatthemeasurable concentrations ofradioactive materials andlevelsofradiation arenothigherthanexpectedonthebasisoftheeffluentmeasurements andmodelingoftheenvironmental exposurepathways'hus, thespecified environmental monitoring programprovidesmeasurements ofradiation andofradioactive materials inthoseexposurepathwaysandfothoseradionuclides whichleadtothehighestpotential radiation exposures ofindividuals resulting fromstationoperation.

Programchangesmaybeproposedbasedonoperational experience.

Deviations arepermitted fromtherequiredsamplingscheduleifspecimens areunobtainable duetohazardous conditions, seasonalunavailability malfunction ofautomatic samplingequipment, andotherlegitimate reasons.Ifspecimens areunobtainable duetosamplingequipment malfunction, aneffortshallbemadetocompletecorrective actionpriortotheendofthenextsamplingperiod.Alldeviations fromthesamplingscheduleshall'bedocumented inthenextAnnualRadioactive EffluentandWasteDisposalreport.Reporting requirements fortheradiological environmental surveillance programaregiveninAppendixBE9.3CENSUSPROGRAMSPECIFICATION 3.12.2-ALAND-USECENSUSSHALLBECONDUCTED ANDSHALLIDENTIFYWITHINADISTANCEOF8KM(5MILES)THELOCATIONINEACHOFTHE16METEOROLOGICAL SECTORSOFTHENEARESTMILKANIMALTHENEARESTRESIDENCE ANDTHENEARESTGARDEN*OFGREATERTHAN50M(500FT~)PRODUCING BROADLEAFVEGETATION

• .Broadleafvegetation samplingofatleastthreedifferent kindsofvegetation maybeperformed atthesiteboundaryineachoftwodirectionsectorswiththehighestpredicted 0/9'inlieuofthegardencensus~Specifications forbroadleafvegetation samplinginTable3.12.1-1,item4Cshallbefollowed,including analysisofcontrolsamplespAy/$JRev.243

Ifalandusecensusidentifies alocation(s) withahigheraverageannualdeposition rate(D/Q)thanacurrentindicator

location, thefollowing shallapply:l.IftheD/Qisatleast20percentgreaterthanapreviously highD/Q,thenewlocationshallbeaddedtotheprogramwithin30daysofdocumented identification ofsamplingfeasibility.

Theindicator locationhavingthelowestD/QmaybedroppedfromtheprogramafterOctober31oftheyearinwhichthelandusecensuswas'conducted.

2.IftheD/Qisnot20percentgreaterthanthepreviously highestD/Q,direction,

.distance, andD/Qwillbeconsidered indecidingwhethertoreplaceoneoftheexistingsamplelocations.

Ifapplicable, replacement shallbewithin30days.Anyevaluations ofpossiblelocationreplacement shouldincludethep'asthistoryofthelocation, availability ofsample,milkproduction history,andotherapplicable environmental conditions.

Alandusecensuswillbeconducted atleastoncepercalendaryearbyadoor-to-door oraerialsurvey,byconsulting localagricultural authorities, orbyanycombination ofthesemethods.9,4INTERLABORATORY COMPARISON PROGRAMSPECIFICATION 3.12.3-ANALYSESSHALLBEPERFORMED ONRADIOACTIVE MATERIALS SUPPLIEDASPARTOFANINTERLABORATORY COMPARISON PROGRAMWHICHHASBEENAPPROVEDBYTHECOMMISSION.

Thelaboratories ofthelicenseeandlicensee's contractors whichperformanalysesshallparticipate intheEnvironmental Protection Agency's(EPA's)Environmental Radioactivity Laboratory Intercomparisons Studies(Crosscheck)

Programoranequivalent programwhichhasbeenapprovedbytheCommission.

Thisparticipation shallincludesomeofthe'determinations (samplemedium-radionuclide combination) thatareofferedbyEPAandthatarealsoincludedinthemonitoring program.Theresultsoftheanalysesofthesecrosscheck samplesshallbeincludedintheannualreport.ADATRev.244 Iftheresultsofan'alyses performed bythelicenseeorlicensee's contractor inconjunction withtheEPAcrosscheck program(orequivalent program)areoutsidethespecified controllimits,thelaboratory shallinvestigate thecauseoftheproblemandtakestepstocorrectit.Theresultsofthisi'nvestigation andcorrective actionshallbeincludedintheAnnualRadiological Environmental Operating Report.Rev.245

'I FIGURE5ENVIRONMENTAL MONITORING LOCATIONS WITHINONEMILEOFTHESSESGOULDISLANDIIII13IIr--~IIIma@Qaor/~fo~l/Q~QS3Ca~Ig,Qpp~m~~m~~eelf5$1~~I,g~52~/3$lT~b$7~bNTILAKE~TAWSITEBOUNDARY1NILESUSQUEHANNA RIVER4svaiuxsamTDOSQtElRY DAT~Rev.2

FIGURE6ENVIRONMENTAL MONITORING LOCATIONS GREATERTHANONEMILEFROMTHESSES15F1T15F1SUSQUEHANNA RIVERINANTICOKE GLENLYON14SHICKSHINNY gnMOCANAQUA 1483T~4E2PONDHILLT12}{2EtlIBERWICKerr.MIFFLINVILLE SSESITiggWAPWALLOPEN

.Tgj~iRI1%2'~TNESCOPECK ggTiRa5NILESCONYNGHAM/1BNILESHAZLETON~mDRSQNCINTER~isaagncrTHERMDLDMNESCENT DQSMERYOATFRev.247 TABLE6OPERATIOHAL RADIOL06ICAL ENVIRDHHENTAL HONITORING PR06RAilPageIoExposurePathwaysandor5leAirborneRadioiodine andParticulates*

lrectRadiation NraaberofSamplesandLocat1ons~12510.4mlMSM-E.O.F.Building12EI4.7mlMSM-BerwlckHospital7GI14mlSE-PPSLHazletonComplex10530.6mlSSM-EastofConfer'sLane,SouthofTowersClub13S60.4mlM-FormerLaydownArea,MestofConfer'sLane1S2Perimeter Fence-0.2ml.NID2Hocanaqua

-4.0mlH253Perimeter Fence-0.2mlNHE283OurabondCorporation

-'1.3mlHHE2FISt.Adalberts Cemetery-5.9mlNNE3S4Perimeter Fence-0.3mlHE301PondIiill/Lily LakeFireCo.-3.4miHE3FIValanlaResidence

-9.1mlHE3G5Mllkes-Barre-Parrish St.Substatlon-16mlHE'S3'MestofSSESAPF-0.2miENE4E1RucklesHI)IRoadPole(t)46422/H35197

-4.8mlENE4GICrestwood Industrial Park-14mlENE'S7Perimeter Fence-0.3mlE5E2BlossFarm-4.5miE6S4Perimeter Fence-0.2mlESE6A4Riverside Restaurant

-0.6mlESESarrpl1ngandContinual sampleroperation withsamplecollection weekly.'*

~Quarterly TypeandRadioiodine Canister:

analyzeweeklyfor1-131Particulate Sample:Analyzeforgrossbetaradioactivity lessthan24hoursfollowing filterchange.Performisotopicanalysisoncomposite sarrple(bylocation) quarterly.

GarrrnaDose:Quarterly.

DATRev.2

Page2oExposurePathwaysandorleNeerofSan@lesandLocations~

6E1St.JamesChurch-4.7miESE659Perimeter Fence-0.2miESE756Perimeter Fence-'0.2miSE7EIHarwoodTransmission LinePoleN2-4.2miSE7G1PPSLHazletonComplex-14miSE'52Perimeter Fence-0.2miSSEBB2LaVallResidence

-1.4miSSE803HowryResidence

-4.0miSSE9S2SecurityFence-0.2mi59D4CountryFolkStore-3.6miS10S1PostSouthofSwitching Station-0.4miSSV10D1RossRymanFarm-3.0miSSM1153SecurityFence-0.3miSM11E1ThomasResidence

-4.7miSV1253Perimeter Fence-0.4miMSM12E1BerwickHospital-4.7miMSV12G1PPSLBloomsburg ServiceCenter-15miMSV'3S2Perimeter Fence-0.4miM13E4KesslerFarm-4.1miV1455Beach.GroveRd.8Confer'sLaneintersection 0.5miVNV14E1CanouseFarm-4.1miVNM15F1LawatskiFarm-5.4miNM1555Perimeter Fence-0.4miNV16S1Perimeter Fence-0.3miNNV1652Perimeter Fence-0.3miNNV16F1HidlayResidence

-7.8NNVSandalingandCollectionFuencTypeandoVaterborne SurfaceDrinkingSedimentfromShoreline 656riverwaterintakeline'S7coolingtowerblowdowndischarge line12H2OanvilleMaterCo.(Approximately 30milesdownstream) 78BellBend,-1.2miSEMonthlycomposite Honthlycomposite Honthlycomposite Semi-annually Ganmaisotopicanalysis.

Composite tritltsnanalysisatleastquarterly.

Grossbetaandgasmaisotopicanalysesmonthly.Composite fortritiumanalysisatleastquarterly.

Gasmaisotopicanalysis'semi-annually.

OATRev.

Page3oExposurePathwaysHIIk~*~FishandInvertebrates FoodProductsNuxberofSamples~atatorationa*1283YoungFarm-2.0miMSM10GIDavisFarm-14mi.SSN'OD2RayRymanFarm-3.5mi.SSM10DlR&CRymanFarm-3.0mi.SSMOutfallarea2HFalls,PA'Approximately 30miHNE)IID1LehnerFarm-3.3.miSVvegetable 12F7LupiniFarm-8.3miWSMvegetable SandalingandCollectionFuencSemi-monthly whenanimalsareonpasture,monthlyotherwise Semi-annually.

Onesample'rom eachoftworeacreationally Important speciesfromanyofthefollowing families:

bullheadcatfish,sunfish,pikes,orperches.AttimeofharvestTypeandoflGammaIsotopicand1-131analysisofeachsample.GasmaIsotopiconedibleportions.

GatnnaI'sotopic onedibleportions.

• Thelocationofsamplesandequipment weredesignedusingtheguidanceInthe8ranchTechnical PositiontoNRCRev.Guide4.8,Rev.1,Nov.1979,Reg.Guide48.1975andORP/SID72-2Environ>>ntal Radioactivity Surveillance Guide.Therefore, theairbornesamplerlocations werebaseduponX/Oand/orD/O.!"Adustloadingstudy(RHC-TR-81-01) concluded thattheassumption ofIforthetransmission correction factorforgrossbetaanalysisofairparticulate samplesIsvalid.Airparticulate samplesneednotbeweighedtodetermine atransmission correction factor."IfamilksampleIsunavailable formorethantwosamplingperiodsfromoneormoreofthelocations, avegetation sampleshallbesubstituted untilasuitablemilklocationIsevaluated.

Suchanoccurrence willbedocumented IntheREHPannualreport.aControlsamplelocation.

bTwo-weekcomposite Ifcalculated dosesduetoconsumption ofwaterexceedonemilliremperyear.Inthesecases,1-131analyseswillbeperformed.

cThesamplecollector willdetermine thespeciesbaseduponavailability, whichmayvaryseasonally andyearly.AI'ATRev.2 TABLE7DETECTION CAPABILITIES FORENVIRONNENTAL SNPLEANALYSISLowerLimitofDetection (LLD)A~nalsisgrossbetaH-3Mn-54Fe-59Co-58Zn-65Zr-95I-131Cs-134Cs-137ea-140La-140WaterQ)Ci~12000301530301b15186015AirborneParticulate orGasCx107x105x106x10FishCikwet130260130260130150MilkQ)Ci~115186015FoodProductsCkwet606080SedimentCd150180DWRev.2 TABLE7(Continued)

TheLLDisthesmallestconcentration ofradioactive materialinasamplethatwillbedetectedwith95percentprobability andwith5percentprobability offalselyconcluding thatablankobservation represents a"real"signal.Foraparticular measurement system(whichmayincluderadiochemical separation):

LLDwhere:4.66sb2.22EVYexp(-A4t)LLDisthe"apriori"lowerlimitofdetection asdefinedabove(aspCiperunitmassorvolume).4sbisthestandarddeviation ofthebackground countingrateorofthecountingrateofablanksampleasappropriate (ascountsperminute)Eisthecountingefficiency (ascountspertransformation)

Visthesamplesize(inunitsofmassorvolume)2.22isthenumberofdisintegrations perminuteperpicocurie Yisthefractional radiochemical yield(whenapplicable)

Aistheradioactive decayconstantfortheparticular radionuclide, and~tistheelapsedtimebetweensamplecollection (orendofthesamplecollection period)andtimeofcounting.

Incalculating theLLDforaradionuclide determined bygamma-ray spectrometry, thebackground shouldincludethecontributions ofotherradio-nuclidesnormallypresentinthesamples(e.g.,potassium-40 milksamples).

TypicalvaluesforE,V,Y,andtshouldbeusedinthecalculations.

Itshouldberecognized thattheLLDisdefinedasanapriori(beforethefact)limitrepresenting thecapability ofameasurement systemandnotasaposteriori (afterthefact)limitforapartic'ular measurement.

LLDfordrinkingwater.DATRev.252

SSTPCYSATHT10.1elect'oofAalssResultsoroseClclationsFordetermination ofcompliance withSSESTechnical Specification doselimits,effluenttotalsshallbebasedonlyonactivitypositively detectedatthe95Xconfidence level.10.2AssinmentofReleasestotheReactorUitsVFordetermination ofcompliance withSSESradioactive effluentdoselimitswhichareona"perreactorunit"basis:a.Effluents fromtheUnit1ReactorBuildingventandtheUnit1TurbineBuildingventshallbeincludedasUnit1releases.

b.Effluents fromthe'nit2ReactorBuildingventandtheUnit2TurbineBuildingventshallbeincludedas.Unit2releases.'.

Effluents fromtheStandbyGasTreatment SystemventshallbeequallydividedbetweenUnit1andUnit2releasetotals.d.Waterborne effluents shallbeequallydividedbetweenUnit1andUnit2releasetotals.10.3Evaluation andMonitorin CriteriaorEffluentPathw'asPotential unmonitored effluentpathwayswillbeevaluated onacase-by-case basis.Periodicsamplingand/orrealistic evaluation wi.llbeperformed inordertodemonstrate thesignificance ofapotential effluentpathway.Resultsofsamplingand/orevaluation maybeusedtoclassifyapotential unmonitored effluentpathwayintooneofthefollowing categories:

a.NotanEffluentPathwa:Realistic evaluation (e.g.,engineering design,systemoperation, radionuclide inventory) demonstrates thatthepathwayhasnopotential forreleaseofradioactive material(Table8).Althoughnotrequired, periodicDATRev.253

'I10'P samplingmayattimesbeperformed toconfirmtheresultoftheevaluation.

b.itffluentPathw:Evaluation and/orperiodicsamplingdemonstrate thatthepathwaymaycontainradioactive effluents, however,theseeffluents maynotbereasonably expectedtoexceed10percentoftheappropriate unrestricted areaHPCvalue(fractional HPCssummedwhenappropriate) listedinTableIIofAppendix8to10CFR20(Table9).A'release pathwaywhichfallsinthiscategorywillbesampledperiodically.

c.SinificantffluentPathwa:Evaluation and/orperiodicsamplingdemonstrate thatthepathwaymaycontainradioactive effluents, andtheseeffluents maybereasonably expectedtoexceed10percentoftheappropriate unrestricted areaHPCvalue(fractional NPCssummedwhenappropriate) listedinTableIIofAppendixBto10CFR20.Areleasepathwaywhichfallsinthiscategorywillbesampledcontinuously.

Analysesofsampleswillbeperformed consistent withtechniques usedforsamplesofthesametypescollected fromnormaleffluentpathways.

Anyradioactive materials detectedinsamplescollected fromeithertheInsignificant ortheSignificant ReleasePathwayswillbeincludedindetermining'compliance withsitedoselimits.Additionally, anysuchoccurrences willbereportedintheAnnualEffluentandWasteDisposalReport.10.4FlowfromtheSGTSVentwhentheSstemisNotinUseWhentheStandbyGasTreatment isnotbeingused,thereremainsasmallamountofflowfromtheSGTSvent.Thisresidualflowisexhaustfromthebatteryroomsinthecontrolstructure.

Becausetherearenoidentifiable sourcesofradioactivity intheserooms,auxiliary particulate andiodinesampleandnoblegasgrabsampleat4-hourintervals arenotrequiredfromtheSGTSventwhentheSGTScontinuous ventmonitorisoutofservice,~rvidedthat-4Rev.2 ek a.theStandbyGasTreatment Systemisnotbeingused,b.thereareproperadministrative controlsinplacetoensurethattherequiredsamplingwillbeginwithin4hoursifthetreatment systemisoperated.

10.50CHSetoinsareUerimitVauesEffluentmonitoralarm/trip setpoints calculated inaccordance withtheODCNshallbeconsidered upperlimitvalues.Higher(lessconservative).

setpoints shallnotbeused,howeverlower(moreconservative) setpoints maybeusedasrequiredtomaximizetheutilityofthemonitor.10.6Defitionof"AroriateTreatment" forLiuidWastesTechnical Specification 3.11.1.3requiresthattheappropriate portionsoftheliquidwas'tetreatment systembeoperableandbeusedtoreduceradioactivity inliquidwastespriortotheirreleasewhenprojected dosesfromeachreactorunittounrestricted areaswouldexceed0.06mremtothetotalbodyor0.2mremtoanyorganina31dayperiod.oThenormaltreatment, whichisconsidered appropriate foreachsubsystem, isasfollows:Filtration isconsidered appropriate treatment fortheLiquidRadwasteLaundryProcessing Subsystem, whichconsistsofhighconductivity liquidwastes,suchasthosefromequipment washdownandpersonnel decontamination facilities, orlaundry.Theatmospheric demineralizer (avendor-supplied systemwhichisdirectedtotheDistillate SampleTank)isconsidered appropriate fortheLiquidRadwasteChemicalProcessing Subsystem.

Rev.255 Demineralization andfiltration areconsidered appropriate treatment forlowconductivity/low organiccontaminant liquidwastesenteringtheLiquidRadwasteProcessing Subsystem (LRMcollection tanks),exceptforbatcheswhichyieldprojected dosespriortotreatment oflessthanorequalto6.45-04mremtothetotalbodyand2.15E-03mremtoanyorgan,wherefiltration aloneisappropriate, oroForbatcheswhichhavenoidentified gammaactivityabovetheTechnical Specification LiquidEffluentLLDlevel(Table4.11.1.1.

1-1),releasewithouttreatment isconsidered appropriate.

BASESTheprojected dosethreshold valuesusedarederivedbydividingthesite-total maximumprojected doseswithouttreatment (0.12and0.4mrem)by31daysandby6,themaximumpossiblenumberofbatchesreleasedperday,toyieldper-batch doseactionlevels.Thetwolevelsof"appropriate" treatment areinplacesoasnottorequireapplication ofdemineralization fortreatinglowactivity, highconductivity water(e.g.,fromCirculating orServiceMaterleakage).

Thiswouldincreasetheoverallefficiency ofthesolidradwasteprogramwhileensuringcalculated dosesremainatasuitablefractionof10CFR50designobjectives andTechnical Specification 3.11.1.21~~t(1)(2)~"'Reference Calculation No.OT-RKB-92-001:

Calculation ofLiquidIsotopeOffsiteDoseConsequences forUseofAtmospheric Demineralizer System,PLI-70360, 2/4/92.DAT'Reference LetterR.K.BarclaytoR.A.Breslin:Demineralizer EffluentResults,PLI-70612, 3/4/92.56Rev.2Atmospheric

10.7itos'rrections Inordertocorrectforairborneeffluentmonitorsamplelineloss,thefollowing correction factorsshallbeappliedtomonitordataandsampleanalysisresults:'NFTHOTSCORCONFACTOSARE~PARTCIIRReactorBuildingUnit1ReactorBuildingUnit2TurbineBuildingUnit1StandbyGasTreatment TurbineBuildingUnit21.51.51.61.51.63.23.23.63.93.6POSTACCIDTVENTMONITORS~CGRRCTIGAFACTIIRR~IODIIIPARTICULATES TurbineBuildingUnit1StandbyGasTreatment TurbineBuildingUnit21.71.61,.74.24.44.3Eachindicated iodineandparticulates concentration shallbemultiplied bytheappropriate correction factortoestimatetheactualconcentration attheinlettothesampleline.10.8Selection ofDataforDetermination ofDoseRateComlianceAirborneeffluentmonitorsetpoints aremaintained inaccordance withSection2.2.toalarmbeforethedoseratelimitsofSpecification 3.11.2.1areexceeded.

Stationalarmresponseprocedures containinstructions forinvestigation andverification ofmonitoralarms.Becausesetpointcalculations mustincludeassumptions aboutthecomposition ofthemonitored

effluent, amonitorhighalarmdoesnotnecessarily indicatethatadoseratelimithasbeenexceeded.

vDATRev.257

Validten-minute averageddatashouldbetheprimaryinformation usedtodetermine thecompliance statusofanincident.

One-minuteaverageddatashouldalsobereviewedifavailable, buttheymayormaynotprovideadditional information depending onthemagnitude ofthereleaseduetothemannerinwhichthemonitorsupdate,valuestobestoredandassociated statistical considerations.

Averagesoveralongerperiodshouldbeusedonlywhendatawithhigherresolution isnotavailable.

Grabsampleanalysesshouldbeperformed wheneverpossibletoconfirmordisprovemonitordata,andtoprovideindication ofthenuclide-.specificcomposition oftheeffluent.

Whengrabsampledataareavailable which,basedonventmonitordata,areindicative oftheperiodofelevatedrelease,doseratecalculations shouldbeperformed usingtheactualeffluentmix.Thedetermination ofcompliance statusshouldnotbebasedonmonitordataalonewhenitispossibletocollectandanalyze'ventsamplewhichwillberepresentative oftheperiodofelevatedrelease.10.9Low-evelRadioactivit intheSewaeTreatmetPlantLikeallsewageprocessing facilities, theSSESsewagetreatment plantcanundercertainconditions receivelowlevelsofradioactive materials.

Themostnotablescenarioiswhenindividuals whoworkon-sitehavebeensubjected tothemedicaladministration ofradiopharmaceuticals fordiagnostic or'herapeutic purposes.

Inthesecases,normalbiological elimination processes caneasilyresultinlevelsofradioactivity insewagetreatment plantsolutions andsuspensions whicharewithinthedetection capabilities oftheassociated samplingandanalysisprogram.Becausedisposalofsewagetreatment plantsludgeby.controlled dispersal onspecified tractsoflandisacommonpractice, thefollowing guidelines havebeenestablished:

a.Allsludgecollected inthesludgeholdingtankshouldbesampledandanalyzedpriortolanddisposaltoquantifyanyDATRev.258 radioactivity presentabovenaturalbackground levels.b.Sludgecontaining nuclideswithshorthalf-lives, forexampleiodine-131, shouldbecontained on-sitetopermitdecaytolessthandetectable levels.c.Whensludgeiscontaminated withnuclideswhichhavehalf-livessufficiently longtomakehold-upfordecayimpractical, thefollowing optionsshouldbeconsidered:

1.Disposeofthesludgeaslowlevelradioactive waste.2.Obtainaspecialpermitpursuanttotherequirements of10CFR20.302.d.Thesewagetreatment planteffluentshouldbesampledmonthlyforradioactivity.

Thiscanbeaccomplished bydrawingasamplefromthechlorinecontactchamber.DATRev.259 11.00ONCONTROTheSupervisor-Environmental Services-Nuclear shallensurethatatotalreviewoftheODCMisperformed duringeacheven-numbered year.Commentsshallbedocumented andrevisions initiate'd asappropriate.

EachODCMpageshallbenumberedandprovidedwithanapprovalanddatebox.TheODCHTableofContentsshallpresentthecurrentrevisiondateforeachpagesothatanymanualholdercancheckmanualcompleteness basedonacurrentTableofContents.

AllODCMrevisions shallbereviewedbyPORCbeforeapprovalbytheManager-Nuclear Technology.

PORCreviewshallbeindicated byPORCchairperson ordesigneesignature onODCHcover.ODCHcopiesshallbeissuedinacontrolled fashionbythestaffoftheNuclearDepartment Library.Thedistribution listshallbemaintained bytheNuclearDepartment LibraryStaff.rAnycommentsonODCMcontentsorproposedrevisions shouldbedirectedtotheSupervisor-Environmental Services-Nuclear.

DATRev.260

~8'I TABLE8SYSTENSCLASSIFIED ASNOTANEFFLUENTPATHWAY(Page1of2)DomesticWaterSYSTENDESCRIPTION REFERENCE RiverWaterHakeuIntakeComressedAirScreensandScreenwash FireProtection WaterFireProtection COFireProtection HalonTurbineBuildinClosedCoolinWaterBuildinDrains:NONRADWaterPretreatment Condensate andRefuelWaterTransferLowPressureAir.Condensate DeminsLubeOilTransferPurification CoolinTowerAcidChlorination Circulatin WaterCondenser TubeCleaninFeedwater Extraction SteamFeedwater HeatersResidualHeatRemovalReactor.CoreIsolation CoolinCoreSrayHihPressureCoolantInjection StandbLiuidControlControlRodDrives(I)PP8LCalculation EC-ENVR-1008 DATBRev.261 TABLE8SYSTENSCLASSIFIED ASNOTANEFFLUENTPATHWAY(Page2of2)SYSTENDESCRIPTION SuressionPoolPrimarContainment VacuumBreakersSuressionPoolCleanuReactorWaterCleanuReactorPressureVesselReactorRecirculation SstemRadwasteChilledMaterSolidRadwasteCementSiloLRWCollection TbandCond.OuterAreaSumsLRWProcessin RadwasteEvaoratorGaseousRadwasteRecombiner ClosedCoolinWaterNitroenStoraeHdroenStoraeSamlinStationsPostAccidentSamlinSstemBassSteamHainSteamIsolation Valves/Nucle'ar'Steam Su1SstemShutoffAutomatic Deressurization SstemHSIVLeakaeControlMoistureSearatorsTurbineSteamSealsElectrohdraulicControlStatorCoolinHainGenerator StormDrainsREFERENCE (I)PP8LCalculation EC-ENVR-1008 rDATRev.262

TABLE9SYSTBlSCLASSIFIED ASINSIGNIFICANT EFFLUENTPATHWAYSYSTBlDESCRIPTION HSealOilCondensate StoraeTankHainTurbineRFPTLubeOilInstrument AirServiceAirTemorarLaundrFacilitSecondSortDAWVolumeReduction Facilit.LowLevelRadwasteHandlinFacilitREFERENCE (1)PP8LCalculation EC-ENVR-1008 (2)SafetyEvaluation NL-90-029:

Temporary LaundryFacility(3)SafetyEvaluation NL-89.-002:

DryActiveWasteVolumeReduction System(4)SafetyEvaluation NL-92-007:

Operation ofLLRWHFatSSESDATRev.263 It0 PORCSUMMARY;ODCHCHANGE12095Section10.3(Evaluation andMonitoring CriteriaforEffluentPathways) hasbeenexpandedtoshowspecificplantsystemsevaluated inthecate'gories NOTANEFFLUENTPATHWAY(listedinnewTable8),andINSIGNIFICANT EFFLUENTPATHWAY(listedinnewTable9).References forthebasesfortheseevaluations areincludedforeachsystemintheTable.Unlessotherwise listed,mostofthesystemswereevaluated inPPKLCalculation EC-ENVR-1008, whichwasperformed in.response toNRCOpenItem91-10-01-.07.

ThisrevisiontotheODCHissubmitted inresponsetoNRCOpenItem91-10-01-08.

JEquations 7,8,17and18arerevisedtoshowtheGammaShielding Factor(S).ThisfactorhasalwaysbeenusedinGASPARcalculations (NRCcodereferenced intheODCH)forwholebodyandskindosefromnoblegaseffluent:

theequations arerevisedtobeconsistent withtheapplication oftheGASPARcode.TheGammaShielding Factor(0.7fortheMaximally-Exposed MemberofthePublic)istakenfromReg.Guide1.109TableE-15.Sections8.1and8.3havebeenrevisedtoreflectthecurrentstateufliquidandsolidradwasteprocessing, respectively.

Figures1,3and4havealsobeenupdatedtoshowchangestoliquidandsolidradwasteprocessing systems,including vendorinterfaces, basedoninformation fromEffluents Management.

Submitted by:Date:1/16/95HealthPhysicist-Operations Technology PENNSYLVANIA POMER5LIGHTCOMPANYSUSQUEHANNA STEAMELECTRICSTATIONOFFSITEDOSECALCULATION MANUALPreparedByi4a-8ZfccReviewedBySupervisor-Environmental ServicesNuclearReviewedBy/eetsngo.ApprovedBHanager-Nuclear Technology Date8>>9SDateDate9Z~-PSDate'Z~a SUMNRYOFODCllCHANGESTable6,Operational Environmental Monitoring Program,hasbeencorrected toshowinformation originally inRevision1oftheODCM(approved 10/14/94).

Someinformation inthistablewasnotedtobeincorrectly carriedintoRevision2(approved 1/20/95).

Table6wasnotintendedtobechangedinanywayinRevision2.Thisinconsistency wasdocumented asastatuscontrolissuein,SOOR95-045;corrections aremadeinresolution tothisSOOR.SlightchangesaremadetoFigure1,LiquidRadwasteSystemFlowDiagram,tomakethepathwayfromthedistillate sampletanktothecoolingtowerblowdownpipeclearer,andtocorrectlabelingofdistillate sampletankpumpsOP-327A,BandLRMsampleTankPumpsOP-305A,B,andC.InSection10.9.c.2, reference 10CFR20.302 ischangedto10CFR20.2002 tobeconsistent withtherevisioninthenumbering ofthisregulation.

Systemclassifications and'references areaddedtoTable8(NotanEffluentPathway)andTable9(Insignificant EffluentPathway).

Table10(Significant EffluentPathway)isaddedwithreferences SectionllisrevisedtostatethatODCMrevisions shallbe.reviewedbyPORCafterapprovalbytheManager-NuclearTechnology.

Rev.3 I'

APPROVAL~AG~DTREVISION~DATE9.0RADIOLOGICAL ENVIRONHENTAL MONITORING PROGRAM.9o1DEFINITIONS@

~~~~~~~~~~~~~~o~~e~~~~~~o~~~~~9.2MONITORING PROGRAM..............-.........

9.3CENSUSPROGRAM............................

9.4INTERLABORATORY COMPARISON PROGRAM........

10.0DOSEASSESSMENT POLICYSTATEMENTS............

10.1SELECTION OFANALYSISRESULTSFORDOSECALCULATIONS 10.2ASSIGNMENT OFRELEASESTOTHEREACTORUNITS10.3EVALUATION ANDMONITORING CRITERIAFOREFFLUENTPATHWAYS10.4FLOWFROMTHESGTSVENTWHENTHESYSTEMISNOTINUSE10.5ODCHSETPOINTS AREUPPERLIMITVALUES10.6DEFINITION OF"APPROPRIATE TREATHENT" FORLIQUIDWASTES10.7MONITORLINE-LOSS CORRECTIONS 10.8SELECTION OFDATAFORDETERMINATION OFDOSERATECOMPLIANCE 10.9LOW-LEVEL RADIOACTIVITY INTHESEWAGETREATMENT PLANT424242434445535353535555555758591/16/951/16/951/16/951/16/951/16/951/16/951/16/951/16/951/16/953/23/953/23/953/23/953/23/953/23/953/23/953/23/951/20/951/20/951/20/951/20/951/20/951/20/951/20/951/20/951/20/953/30/953/30/953/30/953/30/953/30/953/30/953/30/9511.0ODCMREVIEWANDREVISIONCONTROL.............

603/30/953/30/95APPENDIXA-SAMPLECALCULATIONS OFODCHPARAMETERS...........................

APPENDIXB-REPORTING REQUIREMENTS...............

A-1A-2A-3A-4A-5A-6A-7A-8A-9A-10A-llA-12A-13B-1B-2B-3B-42/5/922/5/9212/11/892/5/9210/29/9310/29/9310/29/9310/29/932/5/922/5/9210/29/9310/29/9310/29/9312/11/8910/29/9312/11/8912/11/892/21/922/21/9212/11/892/21/92,3/ll/943/ll/943/ll/943/ll/942/21/922/21/923/ll/943/ll/943/ll/9412/11/893/ll/9412/11/8912/11/89Rev.3 PAGAPPROVALDATEREVISIONDATE5-6cComposite DoseFactors:HaximumHypothetical Child(2pp)....................................5-6c(1,2) 2/18/945-6dWaterIngestion DoseFactors:"HaximumHypothetical Infant(2pp)......................5-6d(1,2) 2/18/943/11/943/11/946Operational Radiological EnviHonitoring Program...........

ronmental

~~~~~~~~~~~~~~~~~~~4849503/23/953/23/953/23/953/30/953/30/953/30/958SystemsClassified asNotanEffluentPathway...

619SystemsClassified asInsignificant Effluentpathway..........................................

10SystemsClassified asSignificant Effluentpathway.........................................

B-lRadiological Environmental Honitoring ProgramAnnualSummary..................................

65B-37Detection Capabilities forEnvironmental SampleAnalysis.................................

51521/16/951/16/953/29/953/29/953/29/951/20/951/20/953/30/953/30/953/30/9512/11/8912/11/89B-2Reporting LevelsforNonroutine Operating Reports.........................................

B-412/11/89Il/9/93D-lDilutionFactorsandTransitTimesforSSESEffluents toDanville, PA.......................

D-l3/ll/943/ll/94

LISTOFFIGURESAPPROVALREVISION~PG~DAE~DEFigure1Figure2Figure3Figure4Figure5Figure6LiquidRadwasteSystemFlowDiagram..........................

OffgasandRecombiner SystemFlowDiagramo~~~~~~~~~~~~~~~~~~~~~~~~~SolidWasteHanagement SystemFlowDiagram..........................

SSESDryContaminated WasteProcess1ngo~~~~~~~~~~~~~~~~~~~~~~~~~~~Environmental Honitoring Locations

,WithinOneHileofSSES...............

Environmental Honitoring Locations GreaterthanOneHilefromSSES.......

383/23/953/30/95391/16/951/20'/95401/16/951/20/95411/16/951/20/95461/16/951/20/95471/16/951/20/95Rev.3V1 l

EVAP.STEAMCONDS.AETUflNTANKPHASESEPARATORS (DECANTATE)

RHRSYSTEMRWCUSYSTEIIREACTORWELLSEALLEAKDRAINREACTORBLDG.DRAINSDAVWELLDRAINSTLNBINEBLDG.DRAINSRADWASTEBLDG.DRAINSLIQUIDRADWASTEfIGURELIQUIDRADWASTESYSTEMFLOWDIAGRAMLIQUIDRADWASTECOLLECTIOH 4SURGETAHKSOT-302ATHRUFOT-301ATHAUDLIOUIDAADWASTEFILTERSOF-302A>BLIOUIORADWASTEDENIHEAALIZER OF-801LIOUIORADWASTESAMPLETAHKSOT-303ATHRUFCOHOENSATE OEMIH.!RESINREGNEAATING TANKLRWCOLLECTION TANKPLAB'SOP-301A,B,CTOWASTEIIIXIHGTANKSOT-307A,BTOSPENTAESIHTANKOT-324LAWSAMPLETANKPNIPSOP-305A8CCOHOENSATE STORAGETANKSOT-522A,BCHEMICALWASTEHEUTRALIZERTANKS1T-130A,B2T-130A,BCSTBEAIIWATERSAMPLESTATIONSAUXBOILERBLOWDOWNS RWCUCHEIIICAL OECOH.LABANDDECOH.DflAIHSCHEM.-WASTENEUTAALIZINGTAIN(PL%PSIP~I30A,B2P~130A,BAADWASTEEVAPORATOR OE-302A,BDISTILLATESAMPLETANKOT-321DISTILLATE SAMPLETANKPCSOP.327A,BAETOCODLINGTOWERSLOW-DOWNPIPELAUMIRYDRAINSREGLAATEO SHOPDRAINSPERSON@.L DECONTAII-INATION(DETEAGENTS)

CASKCLEANINGDRAINSCHEIIICAL WASTETANKOT-314CHEMWASTETANKPLBIPSOP-325A,BCHEIIIGALWASTEPROCESSING SUS-SYSTEII (VENDORSUPPLIED)

EVAPORATOR COHCENTflATE STORAGETANKOT-322TOWASTEIIIXIHOTANKSOT-307A,BLAUNDRYDRAINTANKOT-314A,BDATE9~~~pLAUNDRYDRAINTANKPUMPSOP~318AsBLAUHOAYDRAINFILTERSOF-318A,BLAUNDRYDRAINSAMPLETANKOT-312COHCEHTAATE STORAGETANKOISCH.PNIPOP~32BLALINDAYDRAINSJ4IPLETANKPLIMPSOP.3I9A,b il TABLE6OPERATIONAL RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAMPageof3ExposurePathwaysNumberofSamplesandLocations*

SamplingandCollection FreuencTypeandFreuncofhnalsishirborneRadioiodine andParticulates~

12SI0.4miWSW9BI1.3miSSS40.8miE12EI4.7miWSW7GI14miSE3S20.5miNE7S70.4nuSEIOS30.6miSSW13S60.4miW12GI15miWSWEOFBuildingTransmission LineEnvironmental Laboratory BerwickHospitalPALHazletonComplex'SES Backup.Met.

TowerEndofKline'sRoadEastofConfer'sLane,SouthofTowersClubFormerLaydownArea,WestofConfer'sLane'PN.Bloomsburg ServiceCenter'ontinual sampleroperation withsampleRadioiodine Canister:

analyzecollection weekly.~~

weeklyforI-131Particulate Sample:Analyzeforgrossbetaradioactivity following filterchange.Performisotopicanalysisoncomposite sample(bylocation) quarterly.

DirectRadiation IS2Perimeter Fence-0.2miNID5Mocanaqua SewageTreatment Plant-4.0miN2S3Perimenter Fence-0.2miNNE2B3DurabondCorporation

-1.3miNNE2FISt.Adalberts Cemetery-5.9miNNE3S4Perimeter Fence-0.3miNE4S3WestofSSESAPF-02miENE4E2RucklesHillA;PondHillRoadsIntersection:

4.7miENE4GICrestwood Industrial Park-14miENE'S7Perimeter Fence-0.3miE5E2BlossFarm-4.5mi E6S4Perimeter Fence-0.2miESE6A4Riverside Restaurant

-0.6miESE6EISt.JamesChurch-4.7miESEQuarterly GamniaDose:Quarterly.

Pageof3ExposurePathwaysNumberofSamplesandLocations~

SamplingandCollection 1reuencTypeandFreueneofhnalsis6S97S67EI7GI8S28B28D39S29D4IOSIIODIIIS3IIEI12S312EI12GI13S213E414S514B3ISFI15S516SI16S216FIPerimeter Fence-0.2miESEPerimeter Fence-0.2miSEHarwoodTransmission LinePoleN2-4.2miSEPPN.HazletonComplex-14miSE'erimeter Fence-0.2miSSELaWallResidence

-1.4miSSEMowtyResidence

-4.0miSSESecurityFence-0.2miSCountryFolkStore-3.6miSPostSouthofSwitching Station-0.4miSSWRossRymanFarm-3.0miSSWSecurityFence-0.3miSWThomasResidence

-4.7miSWPerimeter Fence-0.4miWSWBerwickHospital-4.7miWSWPal,Bloomsburg ServiceCenter-15miWSW'erimeter Fence-0.4miWKesslerFarm-4.1miWBeachGroveRd.4Confer'sLaneIntersection 0.5miWNWMoskalukResidence

-1.3miWNWZawatskiFarm-5.4miNWPerimeter Fence-0.4miNWPerimeter Fence0.3miNNWPerimeter Fence-0.3miNNWHidlayResidence

-7.8NNWWaterborne 6S6riverwaterintakeline'S7coolingtowerblowdowndischarge lineMonthlycomposite Monthlycomposite Gatnmaisotopicanalysis.

Composite tritiumanalysisatleastquarterly.

Drinkingl2H2DanvilleWaterCompany{Approxintately 30milesdownstream)

Monthlycomposite Grossbetaandgammaisotopicanalysesmonthly.Composite fortritiumanalysisatleastquarterly.

Rev.3

.I Page3ExposurePathwaysNumberofSamplesandLocations~

SamplingandCollection FreuencTypeandFreuencofhualxisSedimentfromShoreline 7BBellBend-1.2miSESemi-annually Gammaisotopicanalysissemi-annually.

Milk~~~FishandInvertebrates 12B3YoungFarm-2.0miWSWOutfallarea2HFalls,Pa'Approximately 30miNNE)Semi-montMy whenanimalsareonpasture,montMyotherwisc Semi-annually.

Onesample'rom eachoftworeacreationally important speciesfromanyofthefollowing families:

bullheadcatfish,sunfish,pikes,orperches.Gammaisotopicand1-131analysisofeachsampleGammaisotopiconedibleportions.

FoodProductsIIDIZehnerFarm-3.3miSWvegetable AttimeofharvestGatnmaisotopiconedibleportions.

12F7LupiniFarm-8.3miWSWvegetable

~Thelocationofsamplesandequipment weredesignedusingtheguidanceinthcBranchTechnical PositiontoNRCRev.Guide4.8,Rev.I,Nov.1979,Reg.Guide48.1975andORP/SID72-2Environmental Radioactivity Surveillance Guide.Therefore, theairbornesamplerlocations wercbaseduponX/Qand/orD/Q.~~Adustloadingstudy(RMC-TR411) concluded thattheassumption ofIforthetransmission correction factorforgrossbetaanalysisofairparticulate samplesisvalid.Airparticulate samplesneednotbeweighedtodetermine atransmission correction factor."Ifamilksampleisunavailablc formorethantwosamplingperiodsfromoneormorcofthclocations, avegetation sampleshallbesubstituted untilasuitablemilklocationisevaluated.

Suchanoccurrence willbcdocumented intheREMPannualreport.'Controlsamplelocation.

'Two-week composite ifcalculated dosesduetoconsumption ofwaterexceedoncmilliremperyear.Inthesecases,I-131analyseswillbeperformed.

'Thesamplecollector willdetermine thespeciesbaseduponavailability, whichmayvaryseasonally andyearly.OATRtv.3 10.0DOSSSSNTPOICYSTATEHENTS 10.11cioofAn1sisResultsforDoseCalculations Fordetermination ofcompliance withSSESTechnical Specification doselimits,effluenttotalsshallbebasedonlyonactivitypositively detectedatthe95Xconfidence level.10.2AssinmentofReleasestotheReactorUnitsFordetermination ofcompliance withSSESradioactive effluentdoselimitswhichareona"perreactorunit"basis:a.Effluents fromtheUnit1ReactorBuildingventandtheUnit1TurbineBuildingventshallbeincludedasUnit1releases.

.b.Effluents fromtheUnit2ReactorBuildingventandtheUnit2TurbineBuildingventshallbeincludedasUnit2releases.

c.Effluents fromtheStandbyGasTreatment SystemventshallbeequallydividedbetweenUnit1andUnit2releasetotals.d.Waterborne effluents shallbeequallydividedbetweenUnit1andUnit2releasetotals.10.3Evaluation andMoitorinCriteriaforffluentPathwasPotential effluentpathwayswillbeevaluated onacase-by-case basis.Theevaluation willincludeidentification ofsystemswhicharenormallynon-radioactive (asdescribed intheFSAR)butcouldpossiblybecomeradioactive throughinterfaces withradioactive systems(

Reference:

NRCIEBulletinNo.80-10).Theevaluation willdetermine thesignificance ofanypotential effluents pathwaysandextentofsamplingand/ormonitoring required.

Thefrequency ofsamplingormonitoring willbedetermined basedonthepotential forcontamination, thepotential forinadvertent

releases, thepotential levelsofcontamination andreleases, andthepotential impactonstationoffsitedoses.OATRev.353

Resultsofsamplingand/orevaluation willbeusedtoclassifypotential effluentpathwaysintooneofthefollowing categories:

a.NotanEffluentPathwa:Realistic evaluation (e.g.,engineering design,systemoperation, radionuclide inventory) demonstrates thatthepathwayhasnopotential forreleaseofradioactive material(Table8).Althoughnotrequired, periodicsamplingmayattimesbeperformed.to confirmtheresultoftheevaluation.

b.InsinificantffluentPathwa:Evaluation and/orperiodicsamplingdemonstrate thatthepathway.maycontainradioactive effluents, however,theseeffluents maynotbereasonably expectedtoexceed10percentoftheappropriate unrestricted areaHPCvalue(fractional HPCssummedwhenappropriate) listedinTableIIofAppendixBto10CFR20(Table9).Areleasepathwaywhich.fallsinthiscategorywillbesampledperiodically.

c.SinificantEffluentPathwa:Evaluation and/orperiodicsamplingdemonstrate thatthepathwaymaycontainradioactive effluents, andtheseeffluents maybereasonably expectedtoexceed10percentoftheappropriate unrestricted area'HPCvalue(fractional HPCssummedwhenappropriate) listedinTableIIofAppendixBto10CFR20(Table10).Areleasepathwaywhichfallsinthiscategorywillbesampledcontinuously.

Ifsamplingindicates anon-radioactive systemhasbecomecontaminated, furtheruseofthesystemshallberestricted untilthecause.ofthecontamination hasbeencorrected andthesystemisdecontaminated.

Ifcontinued operation ofthesystemascontaminated isnecessary, a10CFR50.59 safetyevaluation oftheoperation ofthesystemasaradioactive systemshallbeperformed immediately bythesystemoperator/engineer.

Thesafetyevaluation willincludeanychangesintheeffluentpathwaysandtheimpactstooffsitedoses.(Ref.NRCIEBulletin80-10).DATRev.354

Positively detectedradioactive materialinsamplescollected fromallairborneandwaterborne offsitereleasepathwayswillbereportedintheAnnualEffluentandWasteDisposalReport.10.,4FlowfromtheSGTSVentwhentheSstemisNotinUseWhentheStandbyGasTreatment isnotbeingused,thereremainsasmallamountofflowfromtheSGTSvent.Thisresidualflowisexhaustfromthebatteryroomsinthecontrolstructure.

Becausetherearenoidentifiable sourcesofradioactivity intheserooms,auxiliary particulate andiodinesampleandnoblegasgrabsampleat4-hourintervals arenotrequired'fromtheSGTSventwhentheSGTScon'tinuous ventmonitorisoutofservice,~y~ovi~d~aa.theStandbyGasTreatment Systemisnotbeingused,b.thereareproperadministrative controlsinplacetoensurethattherequiredsamplingwillbeginwithin4hoursifthetreatment systemisoperated.

10.5ODSetpintsareUerLimitValueEffluentmonitoralarm/trip setpoints calculated inaccordance.

withtheODCHshallbeconsidered upperlimitvalues.Higher(lessconservative) setpoints shallnotbeused,ho'wever=

lower(moreconservative) setpoints maybeusedasrequiredtomaximizetheutilityofthemonitor.10.6Diitionof"AroriateTreatment" forLiuidWastesTechnical Specification 3.11.1.3requiresthattheappropriate portionsoftheliquidwastetreatment systembeoperableandbeusedtoreduceradioactivity inliquidwastespriortotheirreleasewhenprojected dosesfromeachreactorunittounrestricted areaswouldexceed0.06mremtothetotalbodyor0.2mremtoanyorganina31dayperiod.OATRev.355

oThenormaltreatment, whichisconsidered appropriate foreachsubsystem, isasfollows:Filtration isconsidered appropriate treatment fortheLiquidRadwasteLaundryProcessing Subsystem, whichconsistsofhighconductivity liquidwastes,suchasthosefromequipment washdownandpersonnel decontamination facilities, orlaundry.Theatmospheric demineralizer (avendor-supplied systemwhichisdirectedtotheDistilla'te SampleTank)isconsidered appropriate fortheLiquidRadwasteChemicalProcessing Subsystem.

Demineralization andfiltration areconsidered appropriate treatment forlowconductivity/low organiccontaminant liquidwastesenteringtheLiquidRadwasteProcessing Subsystem (LRWcollection tanks),exceptforbatcheswhichyieldprojected dosespriortotreatment oflessthanorequalto6.45-04modemtothetotalbodyand2.15E-03mremtoanyorgan,wherefiltration aloneisappropriate, oroForbatcheswhichhavenoidentified gammaactivityabovetheTechnical Specification LiquidEffluentLLDlevel(Table4.11.1.l.1-1),.releasewithouttreatment isconsidered appropriate.

BASESTheprojected dosethreshold valuesusedarederivedbydividingthesite-total maximumprojected doseswithouttreatment (0.12and0.4mrem)by31daysandby6,themaximumpossiblenumberofbatchesreleasedperday,toyieldper-batch doseactionlevels.Thetwolevelsof"appropriate" treatment areinplacesoasnottorequireapplication ofdemineralization for56OATRev.3 treatinglowactivity, highconductivity water(e.g.,fromCirculating orServiceWaterleakage).

Thiswouldincreasetheoverallefficiency ofthesolidradwasteprogramwhileensuringcalculated dosesremainatasuitablefractionof10CFR50designobjectives andTechnical Specification 3.11.1.2limit.~'"

'0.7Monitr'neossCorrections Inordertocorrectforairborneeffluentmonitorsamplelineloss,thefollowing correction factorsshallbeappliedtomonitordataandsampleanalysisresults:ROUTINFFLUENTMONITORSCORRTIONFACTORSMIOLNE~PTICIReactorBuildingUnit1ReactorBuildingUnit2TurbineBuildingUnit1StandbyGasTreatment TurbineBuildingUnit21.51.51.61.51.63.23.23.63.9'.6POSTACCDENTVENTMONITORSCORRCTONFACTORS~IUIN~PNNCULNINTurbineBuildingUnit1StandbyGasTreatment TurbineBuildingUnit21.71.61.74.24.44,3"'Reference Calculation No.OT-RKB-92-001:

Calculation ofLiquidIsotopeOffsiteDoseConsequences forUseofAtmospheric Demineralizer System,PLI-70360, 2/4/92.'Reference LetterR.K.BarclaytoR.A.Breslin:Demineralizer EffluentResults,PLI-70612, 3/4/92.57Atmospheric

.

Eachindicated iodineandparticulates concentration shallbemultiplied bytheappropriate correction factortoestimatetheactualconcentration attheinlettothesampleline.10.8Selection ofDataforDetermination ofDoseRateComlianceAirborneeffluentmonitorsetpoints aremaintained inaccordance withSection2.2toalarmbeforethedoseratel.imitsofSpecification 3.11.2.1areexceeded.

Stationalarmresponseprocedures containinstructions forinvestigation andverification oFmonitoralarms.Becausesetpointcalculations mustincludeassumptions aboutthecomposition ofthemonitored

effluent, amonitorhighalarmdoesnotnecessarily indicatethatadoseratelimithasbeenexceeded.

'alidten-minute averageddatashouldbetheprimaryinformation usedtodetermine thecompliance statusofanincident.

One-minuteaverageddatashouldalsobereviewedifavailable, buttheymayormaynotprovideadditional information depending onthemagnitude ofthereleaseduetothemannerinwhichthemonitorsupdatevaluestobestoredandassociated statistical considerations.

Averagesoveralongerperiodshouldbeusedonlywhendatawithhigherresolution isnotavailable.

Grabsampleanalysesshouldbeperformed wheneverpossibletoconfirmordisprovemonitordata,andtoprovideindication ofthenuclide-specificcomposition oftheeffluent.

Whengrabsampledataareavailable which,basedonventmonitordata,areindicative oftheperiodofelevatedrelease,doseratecalculations shouldbeperformed usingtheactualeffluentmix.Thedetermination ofcompliance statusshouldnotbebasedonmonitordataalonewhenitispossibletocollectandanalyzeaventsamplewhichwillberepresentative oftheperiodofelevatedrelease.58Rev.3 10.91Radioac'vitintheSeweTramtPntLikeallsewageprocessing facilities, theSSESsewagetreatment plantcanundercertainconditions receivelowlevelsofradioactive materials.

Themostnotablescenarioiswhenindividuals whoworkon-sitehavebeensubjected tothemedicaladministration ofradiopharmaceuticals fordiagnostic ortherapeutic purposes.

Inthesecases,normalbiological elimination processes caneasilyresultinlevelsofradioactivity insewagetreatment plantsolutions andsuspensions whicharewithinthedetection capabilities oftheassociated samplingandanalysisprogram.Becausedisposalofsewagetreatment plantsludgebycontrolled dispersal onspecified tractsoflandisacommonpractice, thefollowing guidelines havebeenestablished:

a.Allsludgecollected inthesludgeholdingtankshouldbesampledandanalyzedpriortolanddisposaltoquantifyanyradioactivity presentabovenaturalbackground levels.b.Sludgecontaining nuclideswithshorthalf-lives, forexampleiodine-131, shouldbecontained on-sitetopermitdec'aytolessthandetectable levels.c.Whensludgeiscontaminated withnuclideswhichhavehalf-livessufficiently longtomakehold-upfordecayimpractical, thefollowing optionsshouldbeconsidered:

l.Disposeofthesludgeaslowlevelradioactive waste.2.Obtainaspecialpermitpursuanttotherequirements of10CFR20.2002.ADATd.Thesewagetreatment plantliquideffluentshouldbesampledmonthlyforradioactivity.

Thiscanbeaccomplished bydrawingasamplefromthechlorinecontactchamber.59Rev.3

11.0ODCMRVWANDREVISIONCONROTheSupervisor-Environmental Services-Nuclear shallensurethatatotalreviewoftheODCHisperformed duringeacheven-numbered year.Commentsshallbedocumented andrevisions initiated asappropriate.

EachODCMpageshallbenumberedandprovidedwithanapprovalanddatebox.TheODCMTableofContentsshallpresentthecurrentrevisiondateforeachpagesothatanymanualholdercancheckmanualcompleteness basedonacurrentTableofContents.

AllODCMrevisions shallbereviewedbyPORCafterapprovalbytheManager-Nuclear Technology.

PORCreviewshallbeindicated byPORCchairperson ordesigneesignature onODCHcover.ODCMcopiesshillbeissuedinacontrolled fashionbythestaffoftheNuclearDepartment Library.Thedistribution listshallbemaintained bytheNuclearDepartment LibraryStaff.AnycommentsonODCMcontentsorproposedrevisions shouldbedirectedtotheSupervisor-Environmental Services-Nuclear.

0>A~5~Rev.360

TABLE8SYSTEMSCLASSIFIED ASNOTANEFFLUENTPATHMAY(Page1of3)SYSTEMDESCRIPTION Domestic.MaterRiverMaterMakeuIntakeComressedAirScreensandScreenwash FireProtection WaterFireProtection COFireProtection HalonTurbineBuildinClosedCoolinMaterBuildinDrains:NONRADWaterPretreatment Condensate andRefuelWaterTransferLowPressureAirCondensate DeminsLubeOilTransferPurification CoolinTowerAcidChlorination Circulatin MaterCondenser TubeCleaninFeedwater Extraction SteamFeedwater HeatersResidualHeatRemovalReactorCoreIsolation CoolinCoreSraHihPressureCoolantInjection StandbLiuidControlControlRodDrivesREFERENCE (1)PP5LCalculation EC-ENVR-1008 Rev.361 TABLE8SYSTB5CLASSIFIED ASNOTANEFFLUENTPATHWAY(Page2of3)SYSTENDESCRIPTION SuressionPoolPrimarContainment VacuumBreakersSuressionPoolCleanuReactorWaterCleanuReactorPressureVesselReactorRecirculation SstemRadwasteChilledWaterSolidRadwasteCementSiloLRWCollection TbandCond.OuterAreaSumsLRWProcessin RadwasteEvaoratorGaseousRadwasteRecombiner ClosedCoolinWaterNitroenStoraeHdroenStoraeSamlinStationsPostAccidentSamlinSstemBassSteamMainSteamIsolation Valves/NuclearSteamSu1,SstemShutoffAutomatic Deressurization SstemMSIVLeakaeControlMoistureSearatorsTurbineSteamSealsElectrohdraulicControlStatorCoolinMainGenerator StormDrainsREFERENCE (1)PP8LCalculation EC-ENVR-1008 DATRev.362 f'

TABLE8SYSTEMSCLASSIFIED ASNOTANEFFLUENTPATHWAY(Page3of3)SYSTEMDESCRIPTION MakeuDemineral izersFuelOilContainment Instrument GasControlStructure ChilledWaterTurbineBld.ChilledWaterReactorBld.ChilledMaterAuxiliarBoilersfuelPoolCoolinFuelPoolDemineralizers FuelPoolsTemorarySDHRSstemREFERENCE Rev.363 TABLE9SYSTENSCLASSIFIED ASINSIGNIFICANT EFFLUENTPATHWAYSYSTEMDESCRIPTION HSealOilCondensate StoraeTankandBermHainTurbineRFPTLubeOilInstrument AirServiceAir.TemorarLaundrFacilitSecondSortDAWVolumeReduction FacilitLowLevelRadwasteHandlinFacilityREFERENCE Rev.3 TABLE10SYSTENSCLASSIFIED ASSIGNIFICANT EFFLUENTPATHWAYSYSTEHDESCRIPTION LiuidWasteManaementSstemsGaseousWasteManaementSystemsREFERENCE (1)PPELCalculation EC-ENVR-1008 (2)SafetyEvaluation NL-90-029:

Temporary LaundryFacility(3)SafetyEvaluation NL-89-002:

DryActiveWasteVolumeReduction System(4)SafetyEvaluation NL-92-007:

Operation ofLLRWHFatSSES(5)SSESFSARChapter11.2(6)SSESFSARChapter11.3-(7)SafetyEvaluation NL-95-001:

Refueling OutageDecayHeatRemovalandTie-InoftheSDHRTemporary CoolingEquipment.

rvDATRev.3 P

PENNSYLVANIA POWER8LLIGHTCOMPANYSUSQUEHANNA STEAMELECTRICSTATIONOFFSITEDOSECALCULATION MANUALRevision4PreparedByDateReviewedBySupervisor-Environmental ServicesNuclearM~sz/eetsngo.ApprovedByHanager-Nuclear Technology DateDateOate SUMMARYOFODCMCHANGESThreemilksamplingstations(IOGI,IOD2andIODI)wereinadvertently deletedinTable6,Rev.3,andarerestoredherein.Thesedeletions werenotnotedinreviewofTable6,Rev.3,whichwassubmitted inresolution toSOOR95-045;Thenameoftherestaurant atTLDstation6A4hasbeeadeletedtomakethedescription moregeneric,inresponsetoaPORCcommentfromthe.meetingonMarch30,1995.Rev.4 TABLEAPPROVALREVISIONJPPGE~0AEDATE5-6cComposite DoseFactors:HaximumHypothetical Child(2pp)....................................5-6c(1,2) 2/18/945-6dWaterIngestion DoseFactors:HaximumHypothetical Infant(2pp)......................5-6d(1,2) 2/18/943/11/943/ll/946.Operational Radiological Environmental Honitoring Program..............................

4849504/17/953/23'/954/17/95'.4/20/953/30/954/20/951/20/951/20/953/30/953/30/953/30/951/16/951/1'6/953/29/953/29/953/29/958SystemsClassified asNotanEffluentPathway...

619SystemsClassified asInsignificant Effluentathway.........................................

p10'SystemsClassified asSignificant Effluent~~pathway~~~~~~~~~~~~~~~~~~~~~~~~'~~~~~~~~~~~~~~~B-1Radiological Environmental Honitoring ProgramAnnualSummary.................................;

658-312/11/8912/11/897Detection Capabilities forEnvironmental SampleAnalysis.................................

5152B-2Reporting LevelsforNonroutine Operating eports....'.....................................

RB-412/11/8911/9/93D-lDilutionFactorsandTransitTimesforSSESEffluents toDanville, PA.......................

D-l3/11/943/ll/94 TABLE6OPERATIONAL RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAMPage1oExposurePathwaysNumberofSamplesandLocations*

SamplingandCollection FreuencTypeandFreuencofhnalsishirborneRadioiodine andParticulates~

12SI0.4miWSW9BI1.3miS5S40.8miE12EI4.7miWSW7GI14miSE3S20.5miNE7S70.4miSEIOS30.6miSSW.13S60.4miW12GI15miWSWEOFBuildingTransmission LineEnvironmental Laboratory BerwickHospitalPP&LHazletonComplex'SES BackupMet.TowerEndofKline'sRoadEastofConfer'sLane,SouthofTowersClubFormerLaydownArea,WestofConfer'sLane'P&LBloomsburg ServiceCenter'ontinual sampleroperation withsamplecollection weekly."Radioiodine Canister:

analyzeweeklyfor1-131Particulate Sample:Analyzeforgrossbetaradioactivity following filterchange.Performisotopicanalysisoncomposite sample(bylocation) quarterly.

DirectRadiation IS2Perimeter Fence-0.2miNID5Mocanaqua SewageTreatment Plant-4.0miN2S3Perimenter Fence-0.2miNNE2B3DurabondCorporation

-1.3miNNE2FISt.Adalberts Cemetery-5.9miNNE3S4Perimeter Fence-0.3miNE4S3WestofSSESAPF-0.2miENE4E2RucklesHill&PondHillRoadsIntersection:

4.7miENE4GICrcstwood Industrial Park-14miENE'S7Perimeter Fence-0.3miE5E2BlossFarm-4.5miE6S4Perimeter Fence-0.2miESE6A4Restaurant

-0.6miESE6EISt.JamesChurch-4.7miESEQuarterly GammaDose:Quarterly.

nnfF.Rev.4

Page3ExposurePathwaysNumberofSamplesandLocations*

SamplingandCollection FreuencTypeandFreuencofhnalsisSedimentfromShoreline 7BBellBend-1.2miSESemi-annually Gammaisotopicanalysissemi-annually.

Milk~~~12B3YoungFarm-2.0miWSWIOGIDavisFarm-14.0mi.SSW'OD2RayRymanFarm-3.5mi.SSW10DIKLCRymanFarm-3.0mi.SSWSemi-monthly whenanimalsareonpasture,monthlyotherwise GammaisotopicandI-131analysisofeachsampleFishandInvertebrates Outfallarea2HFalls,Pa'Approximately 30miNNE)Semi-annually.

Onesample'rom eachoftworeacreationally important speciesfromanyofthefollowing families:

bullheadcatfish,sunfish,pikes,orperches.Gammaisotopiconedibleportioils.

FoodProducts11DIZehnerFarm-3.3miSWvegetable AttimeofharvestGammaisotopiconediblePoftioilS.

12F7LupiniFarm-8.3miWSWvegetable

~Thelocationofsamplesandequipmcnt weredesignedusingtheguidanceintheBranchTechnical PositiontoNRCRev.Guide4.8,Rev.I,Nov.1979,Reg.Guide48.1975andORP/SID72-2Environmental Radioactivity Surveillance Guide.Therefore, theairbornesamplerlocations werebaseduponX/gand/orD/Q.~'Adustloadingstudy(RMC-TR-8141) concluded thattheassumption ofIforthetransmission correction factorforgrossbetaanalysisofairparticulate samplesisvalid.Airparticulate samplesneednotbeweighedtodetermine atransmission correction factor.~~'Ifamilksampleisunavailable formorethantwosamplingperiodsfromoneormoreofthelocations, avegetation sampleshallbesubstituted untilasuitablemilklocationisevaluated.

Suchanoccurrence willbedocumented intheREMPannualreport.'Controlsamplelocation.

rwo-weekcomposite ifcalculated dosesduetoconsumption ofwaterexceedonemilliremperyear.Inthesecases,1-131analyseswillbeperformed.

'Thesamplecollector willde'termine thespeciesbaseduponavailability, whichmayvaryseasonally andyearly.DAT I

PENNSYLVANIA POWER&LIGHTCOMPANYSUSQUEHANNA STEAMELECTRICSTATIONQFFSITEDOSECALCULATION MANUALRevision6Preparedby:Date:Reviewedby:Supervisor Environmental Services-NuclearDate:Reviewedby:PORC/Meeting No.Date:Approvedby:./Manager-NuclearTechnology Date:7 SUMMARYOFODCMCHANGES1.TheIntroduction hasbeenrevisedtospecifythatreference toMPClimitsof10CFR20AppendixBinthedocumentappliestothoselimitsineffectpriortoJanuary1,1994,andcontinuing ineffectuntilsuchtimethatrevised10CFR20AppendixBlimitsareimplemented atSSES.\2.Adescription ofsystemswithNRCI/EBulletin80-10applicability hasbeenaddedtoSection10.3.Reference ismadetoTable11,whichliststhe80-10systemsbynumberandname.3.Table9isrevisedtoincludeRefuelWaterStorageTankwithCondensate StorageTankandBerm,andH2SealOilwithMainTurbine/RFPT LubeOil.TheSewageTreatment PlantisaddedtoTable9.Reference notesforthesechangesarenowlocatedintheappropriate tables.4.Table11(SystemswithNRCI/EBulletin80-10Applicability) isaddedtotheODCM.TheSewageTreatment PlantisaddedtoTable11inresponsetoPORCMeeting95-098ActionItemE05532.5.Section11(ODCMReviewandRevisionControl)isrepaginated tofollowTables8-11ofSection10.Reference torevisioninaccordance withNEPM-QA-1011 isadded,whichissubmitted asanActiontoPreventRecurrence inSOOR95-045.Thedistribution ofODCMcopiesisrevisedtoindicateSSESDocumentControlServices, whichreplacesthestaffoftheNuclearDepartme'nt Library.6.Thisrevisiondoesnotreducetheaccuracyorreliability ofdosecalculations orsetpointdeterminations.

Rev.5

TABLEOFCONTENTS

1.0INTRODUCTION

~paeApprovalDate7/14/957/14/951119/93Rev>sionDate7/20/957/20/953/11/942.0SETPOINTS 2.1Waterborne EffluentMonitors2.2AirborneEffluentMonitors3.0WATERBORNE EFFLUENTCONCENTRATION MEASUREMENTS 4.0AIRBORNEEFFLUENTDOSERATES4.1NobleGases4.2Radionuclides OtherThanNobleGases5.0INDIVIDUAL DOSEDUETOWATERBORNE EFFLUENT5.1FishPathwayLiquidEffluentDoseCalculation Methodology 5.2PotableWaterPathwayEffluentDoseCalculation Methodology 5.3Shoreline ExposurePathway5.4Projected DoseFromLiquidEffluent6.0INDIVIDUAL DOSEDUETOAIRBORNEEFFLUENT6.1NobleGases6.2Radionuclides OtherThanNobleGases7.0'OTALDOSE9101112141515161718192023242425262727282930312/5/922/5/9212/11/892/5/9212/11/8912/11/892/5/9212/11/8912/11/89'1/21/922/5/922/5/922/5/921/16/951/16/952/11/922/5/9212/11/8912/1/9210/29/932/18/9411/9/9311/9/9311/9/932/18/9411/9/9310/29/9310/29/9310/29/9310/29/931/16/9510/29/932/21/92'/21/92 12/11/892/21/9212/11/8912/11/892/21/9212/11/8912/11/8911/25/922/21/922/21/922/21/921/20/951/20/952/21/922/21/9212/11/8912/4/923/11/943/11/943/11/943/11/94.3/11/943/11/943/11/943/11/943/11/943/11/943/11/941/20/953/11/94Rev.5

8.0 OPERABIUTY

OFWASTETREATMENT SYSTEMS8.1LiquidWasteTreatment 8.2GaseousWasteTreatment 8.3SolidWasteTreatment

9.0 RADIOLOGICAL

ENVIRONMENTAL MONITORING PROGRAM9.1Definitions 9.2Monitoring Program9.3CensusProgram9.4Intertaboratory Comparison Program~Pae32323334353637424242434445ApprovalOats10/29/931/16/951/16/951/16/951/16/951/16/951/16/951/16/951/16/951/16/951/16/951/16/95.1/16/95RevisionDate3/11/941/20/951/20/951/20/951/20/951/20/951/20/951/20/951/20/951/20/95.1/20/951/20/951/20/9510.0DOSEASSESSMENT POLICYSTATEMENTS 5310.1Selection ofAnalysisResultsforDoseCalculations 53~10.2Assignment ofReleasestotheReactorUnits5310.3Evaluation andMonitoring CriteriaforEffluent53Pathways10.4FlowFromtheSgtsVentWhentheSystemisNot54InUse7/14/957/14/957/14/957/14/957/14/957/20/957/20/957/20/957/20/957/20/9510.5ODCMSetpoints AreUpperLimitValues10.6Definition of"Appropriate Treatment" forLiquidWastes10.7MonitorLine-Loss Corrections 10.8Selection ofDataForDetermination ofDoseRateCompliance 10.9Low-Level Radioactivity intheSewageTreatment Plant11.0ODCMREVIEWANDREVISIONCONTROL5656585960687/14/957/14/957/14/957/14/957/14/957/14/957/20/957/20/957/20/957/20/957/20/957/20/95DATRev.5 AppendixA-SampleCalculations ofODCMParameters AppendixB-Reporting Requirements

~PaeA-1A-2A-3AQA-5AWA-7A-8A-9A-10A-11A-12A-13B-1B-2B-3BPApprovalDate2/5/922/5/9212/11/892/5/9210/29/9310/29/9310/29/9310/29/932/5/922/5/9210/29/9310/29/9310/29/9312/11/8910/29/9312/11/8912/11/89RevisionDate2/21/922/21/9212/11/892/21/923/11/943/11/943/11/943/11/942/21/922/21/923/11/943/11/943/11/9412/11/893/11/9412/11/8912/11/89AppendixC-SiteSpecificInformation UsedbyGasparCodeC-1112/11/8912/11/89AppendixD-SiteSpecificInformation UsedbyLadtapCode10/10/9410/14/94Rev.5 TableLISTOFTABLESApprovalRevision~pae1Radiological EffluentObjectives andStandards 2DoseFactorsforNobleGases3SampleAnnualAverageRelativeConcentrations andDeposition Rates4DoseFactorsforInhalation, Ingestion andGroundExposurePathways:

Radionuciides OtherThanNobleGases5-1aDoseFactorsforFishPathway,MaximumHypothetical Adult(2pp)5-1bDoseFactorsforFishPathway,MaximumHypothetical Teen(2pp)5-1cDoseFactorsforFishPathway,MaximumHypothetical Child(2pp)5-2aDoseFactorsforPotableWaterPathway,MaximumHypothetical Adult(2pp)5-2bDoseFactorsforPotableWaterPathway,MaximumHypothetical Teen(2pp)5-2cDoseFactorsforPotableWaterPathway,MaximumHypothetical Child(2pp)5-2dDoseFactorsforPotableWaterPathway,MaximumHypothetical Infant(2pp)5-3Radioactive DecayConstants 5QDilutionFactorsandTransitTimesforSSESEffluents toDanville, PA5-5DoseFactorsforShoreExposurePathway,AllAgeGroups(2pp)5<aComposite DoseFactors:MaximumHypothetical Adult(2pp)5-6bComposite DoseFactors:MaximumHypothetical Teen(2pp)1819~205-1a(1,2)5-1b(1,2) 5-1c(1,2)5-2a(1,2) 5-2b(1,2) 5-2c(1,2) 5-2d(1,2) 5-35A(1,2)'5-5(1,2) 5-6a(1,2) 5-6b(1,2) 11/9/933/11/942/5/922/21/9211/9/933/11/9412/1/9212/4/9210/10/9410/14/9410/10/9410/14/9410/10/9410/14/9410/29/933/11/9410/29/933/11/9410/29/933/11/9410/29/933/11/9410/29/933/11/9410/29/933/11/9410/29/933/11/9410/10/9410/14/9410/10/9410/14/94DATRev.5IV Table5-6cComposite DoseFactor:MaximumHypothetical Child(2pp)15-6dWaterIngestion DoseFactors:MaximumHypothetical Infant(2pp)~Pae5-6c(1,2) 5-6d(1,2)

ApprovalRevisionDateOate2/18/943/11/942/18/943/11/946Operational Radiological Environmental Monitoring Program7Detection Capabilities forEnvironmental SampleAnalysis48495051524/17/953/23/954/17/951/16/951/16/95,4/20/953/30/954/20/951/20/951/20/958SystemsClassified asNotanEffluentPathway9SystemsClassified asInsignificant EffluentPathway10SystemsClassified asSignificant EffluentPathway11SystemswithNRCI/EBulletin80-10Applicability B-1Radiological Environmental Monitoring ProgramAnnualSummaryB-2Reporting LevelsforNonroutine Operating ReportsD-1DilutionFactorsandTransitTimesforSSESEffluents toDanville, PA62656667B-3B-4D-17/14/957/20/958/7/95'/20/95 7/14/957/20/958/7/957/20/9512/11/89'2/11/89 12/11/8912/11/8911/9/933/11/94SewageTreatment PlantaddedinresponsetoPORCMeeting95-098ActionItemE05532.OATRev.5

LlSTOFFIGVRES~Fi~u~PaeApprovalDateRevisionDate1LiquidRadwasteSystemFlowDiagram2OffgasandRecombiner SystemFlowDiagram3SolidWasteManagement SystemFlowDiagram4SSESDryContaminated WasteProcessing 5Environmental Monitoring Locations WithinOneMileofSSES6Environmental Monitoring Locations GreaterthanOneMilefromSSES3839404146473/23/951/16/951/16/951/16/951/16/951/16/953/30/951/20/95,1/20/951/20/951/20/951/20/95

1.0INTRODUCTION

Thepurposeofthismanualistoprovidetheparameters andmethodology tobeusedincalculating offsitedosesandeffluentmonitorsetpoints fortheSusquehanna SteamElectricStation,Units1and2.Includedaremethodsfordetermining maximumindividual, whole-body, andorgandosesduetowaterborne andairborneeffluents toensurecompliance withthedoselimitations intheTechnical Specifications.

Methodsareincludedforperforming dosecalculations toensurecompliance withthewaterborne andairbornetreatment systemoperability sectionsoftheTechnical Specifications.

Thismanualincludesthemethodsusedfordetermining quarterly individual dosesforinclusion inAnnualEffluentandWasteDisposalReports.Thedosemodelsconsidertworeleasemodes:airborneandwaterborne.

Allairborneeffluents aretreatedasground-level releases.

DosetoeachofthesevenorganslistedinRegulatory Guide1.109(bone,liver,totalbody,thyroid,kidney,lung,andGI-LLI)arecomputedbasedontheindividual nuclidecomposition oftheeffluent.

Thelargestofthedosesarecomparedto10CFR59,AppendixIdesignobjectives.

Liquideffluents discharged intoariverundergomixingpriortoconsumption aseitherpotablewaterorthroughthefishpathway.ForreleasestotheSusquehanna River,rivermodeldilutionfactorsareused.DosestothesevenTcriticalorgansaredetermined fromindividual nuclidecontributions andarecomparedtothe10CFR50AppendixIdesignobjectives.

Compliance withthe10CFR20maximumpermissible concentrations isdoneonabatch-by-batch basispriortodischarge.

Henceforth inthisdocument, reference toMPClimitsof10CFR20AppendixBappliestothoselimitsineffectpriortoJanuary1,1994,andcontinuing ineffectuntilsuchtimethatrevised10CFR20AppendixBlimitsareimplemented atSSES.OATRev.5 Thismanualdiscusses themethodology tobeusedindetermining eNuentmonitoralarm/trip setpoints tobeusedtoensurecompliance withtheinstantaneous releaseratelimitsintheTechnical Specifications.

Methodsaredescribed fordetermining theannualcumulative dosetoarealindividual fromliquideNuents,gaseouseNuents,anddirectradiation forcriticalorganstoensurecompliance with40CFR190limits.Thecalculational methodology fordosesarebasedonmodelsanddatathatmakeitunlikelytosubstantially underestimate theactualexposureofanindividual throughanyoftheappropriate pathways.

TheRadiological Environmental Monitoring, Programisdescribed inSection9.0ofthemanual,whichincludestheannuallandusecensussurveyandinterlaboratory comparison program.,

Itistheresponsibility oftheSuperintendent ofPlant-Susquehanna toensurethatthismanualisusedinperformance ofthesurveillance requirements andforcompliance withthelimitingconditions ofoperations statedintheTechnical Specifications.

Itistheresponsibility oftheManager-Nuclear Technology toensureadequacyandcorrectness ofcalculational approaches.

Rev.5 014 10.0DOSEASSESSMENT POLICYSTATEMENTS 10.1Selection ofAnalsisResultsforDoseCalculations Fordetermination ofcompliance withSSESTechnical Specificatio doselimits,effluenttotalsshallbebasedonlyonactivitypositively detectedatthe95%confidence level.10.2AssinmentofReleasestotheReactorUnits'Fordetermination ofcompliance withSSESradioactive effluentdoselimitswhichareona"perreactorunit"basis:a.Effluents fromtheUnit1ReactorBuildingventandtheUnit1TurbineBuildingve'ntshallbeincludedasUnit1releases.

b.Effluents fromtheUnit2ReactorBuildingventandtheUnit2TurbineBuildingventshallbeincludedasUnit2releases.

c.Effluents fromtheStandbyGasTreatment SystemventshallbeequallydividedbetweenUnit1andUnit2releasetotals.'d.Waterborne effluents shallbeequallydividedbetweenUnit1andUnit2releasetotals.10.3Evaluation andMonitorin CriteriaforEffluentPathwasPotential:effluent pathwayswillbeevaluated onacase-by-case basis.Theevaluation willincludeidentification ofsystemswhicharenormallynon-radioactive (asdescribed intheFSAR)butcouldpossiblybecomeradioactive throughinterfaces withradioactive systems(

Reference:

NRCIEBulletinNo.80-10).Theevaluation willdetermine thesignificance ofRev.553 I'P4 anypotential effluents pathwaysandextentofsamplingand/ormonitoring required.

Thefrequency ofsamplingormonitoring willbedetermined basedonthepotential forcontamination, thepotential forinadvertent

releases, thepotential levelsofcontamination andreleases, andthepotential impactonstationoffsitedoses.Resultsofsamplingand/orevaluation willbeusedtoclassifypotential effluentpathwaysintooneofthefollowing categories:

a.NotanEffluentPathwa:Realistic evaluation (e.g.,engineering design,systemoperation, radionuclide inventory) demonstrates thatthepathwayhasnopotential forreleaseofradioactive material(Table8).Althoughnotrequired, periodicsamplingmayattimesbeperformed toconfirmtheresultoftheevaluation.

b.InsinificantEffluentPathwa:Evaluation and/orperiodicsamplingdemonstrate thatthepathwaymaycontainradioactive effluents, however,theseeffluents maynotbereasonably expectedtoexceed10percentoftheappropriate unrestricted areaMPCvalue(fractional MPCssummedwhenappropriate) listedinTableIIofAppendixBto10CFR20(Table9).Areleasepathwaywhichfallsinthiscategorywillbesampledperiodically.

c.SinificantEffluentPathwa:Evaluation and/orperiodicsamplingdemonstrate thatthepathwaymaycontainradioactive effluents, andtheseeffluents maybereasonably expectedtoexceed10percentoftheappropriate unrestricted areaMPCvalue(fractional MPCssummedwhenappropriate) listedinTableIIofAppendixBto10CFR20(Table10).Areleasepathwaywhichfallsinthiscategorywillbesampledcontinuously.

Rev.554 Ifsamplingindicates anon-radioactive systemhasbecomecontaminated, furtheruseofthesystemshallberestricted untilthecauseofthecontamination hasbeencorrected andthesystemisdecontaminated.

Ifcontinued operation ofthesystemascontaminated isnecessary, a10CFR50.59 safetyevaluation oftheoperation ofthesystemasaradioactive systemshallbeperformed immediately bythesystemoperator/engineer.

Thesafetyevaluation willincludeanychangesintheeffluentpathwaysandtheimpactstooffsitedoses.(Ref.NRCIEBulletin80-10).SystemswithNRCI/EBulletinapplicability aredesignedtobeusedasnon-radioactive, butwhichcouldpossiblybecomeradioactive throughinterface(s) withradioactive systems,andwhichhaveapathforunmonitored and/oruncontrolled releasetotheenvironment.

(Table11)Positively detectedradioactive materialinsamplescollected fromallairborneandwaterborne offsitereleasepathwayswillbereportedintheAnnualEffluentandWasteDisposalReport.10.4FlowfromtheSGTSVentwhentheSstemisNotinUseWhentheStandbyGasTreatment isnotbeingused,thereremainsasmallamountofflowfromtheSGTSvent.Thisresidualflowisexhaustfromthebatteryroomsinthecontrolstructure.

'Becausetherearenoidentifiable sourcesofradioactivity intheserooms,auxiliary particulate andiodinesampleandnoblegasgrabsampleat4-hourintervals arenotrequiredfromtheSGTSventwhentheSGTScontinuous ventmonitorisoutofservice,trrovided that-a.theStandbyGasTreatment Systemisnotbeingused,Rev.555 b.thereareproperadministrative controlsinplacetoensurethattherequiredsamplingwillbeginwithin4hoursifthetreatment systemisoperated.

10.5ODCMSetpintsareUerLimitValuesEffluentmonitoralarm/trip setpoints calculated inaccordance withtheODCMshallbeconsidered upperlimitvalues.Higher(lessconservative) setpoints shallnotbeused,howeverlower(moreconservative) setpoints maybeusedasrequiredtomaximizetheutilityofthemonitor.10.6Definition of"AroriateTreatment" forLiuidWastesTechnical Specification 3.11.1.3requiresthattheappropriate portionsoftheliquidwastetreatment systembeoperableandbeusedtoreduceradioactivity inliquidwastespriortotheirreleasewhenprojected dosesfromeachreactorunittounrestricted areaswouldexceed0.06mremtothetotalbodyor0.2mremtoanyorganina31dayperiod.~Thenormaltreatment, whichisconsidered appropriate foreachsubsystem, isasfollows:Filtration isconsidered appropriate treatment fortheLiquidRadwasteLaundryProcessing Subsystem, whichconsistsofhighconductivity liquidwastes,suchasthosefromequipment washdownandpersonnel decontamination facilities, orlaundry.Theatmospheric demineralizer (avendor-supplied systemwhichisdirectedtotheDistillate SampleTank)isconsidered appropriate fortheLiquidRadwasteChemicalProcessing Subsystem.

Rev.556 4,I4 Demineralization andfiltration areconsidered appropriate treatment forlowconductivity/low organiccontaminant liquidwastesenteringtheLiquidRadwasteProcessing Subsystem (LRWcollection tanks),exceptforbatcheswhichyieldprojected dosespriortdtreatment oflessthanorequalto6.45-04mremtothetotalbodyand2.15E-03mremtoanyorgan,wherefiltration aloneisappropriate, of~Forbatcheswhichhavenoidentified gammaactivityabovetheTechnical Specification LiquidEffluentLLDlevel(Table4.11.1.1.1-1

),releasewithouttreatment isconsidered appropriate.

BASESTheprojected dosethreshold valuesusedarederivedbydividingthesite-total maximumprojected doseswithouttreatment (0.12and0.4mrem)by31daysandby6,themaximumpossiblenumberofbatchesreleasedperday,toyieldper-batch doseactionlevels.Thetwolevelsof"appropriate" treatment areinplacesoasnot'torequireapplication ofdemineralization fortreatinglowactivity, highconductivity water(e.g.,fromCirculating orServiceWaterleakage).

Thiswouldincreasetheoverallefficiency ofthesolidradwasteprogramwhileensuringcalculated dosesremainatasuitablefractionof10CFR50designobjectives andTechnical Specification 3.11.1.2limit."'"'.

"'Reference Calculation No.OT-RKB-92-001:

Calculation ofLiquidIsotopeOffsiteDoseConsequences forUseofAtmospheric Demineralizer System,PLI-70360, 2/4/92.Rev.557

10.7MonitorLineLossCorrections InordertocorrectforairborneeNuentmonitorsamplelineloss,thefollowing correction factorsshallbeappliedtomonitordataandsampleanalysisresults:CORRECTION FACTORSRoutineEffluentMonitorsiodineParticulates ReactorBuildingUnit1ReactorBuildingUnit2TurbineBuildingUnit1StandbyGasTreatment TurbineBuildingUnit21.51.51.61.51.63.23.23.63.93.6.CORRECTION FACTORSPost-Accident VentMonitorsiodineParticulates TurbineBuildingUnit1StandbyGasTreatment TurbineBuildingUnit21.71.61.74.2'44.3Eachindicated iodineandparticulates concentration shallbemultiplied bytheappropriate correction factortoestimatetheactualconcentration attheinlettothesampleline.+Reference LetterR.K.BarclaytoR.A.Breslin:Atmospheric Demineralizer ENuentResults,PLI-70612, 3/4/92.DATRev.558

10.8Selection ofDataforDetermination ofDoseRateComlianceAirborneeffluentmonitorsetpoints aremaintained inaccordance withSection2.2toalarmbeforethedoseratelimitsofSpecification 3.11.2.1areexceeded.

Stationalarmresponseprocedures containinstructions forinvestigation andverification ofmonitoralarms.Becausesetpointcalculations mustincludeassumptions aboutthecomposition ofthemonitored

effluent, amonitorhighalarmdoesnotnecessarily indicatethatadoseratelimithasbeenexceeded.

Validten-minute averageddatashouldbetheprimaryinformation usedtodetermine thecompliance statusofanincident.

One-minute averaged~datashouldalsobereviewedifavailable, buttheymayormaynotprovideadditional information depending onthemagnitude ofthereleaseduetothemannerinwhichthemonitorsupdatevaluestobestoredandassociated statistical considerations.

Averagesoveralongerperiodshouldbeusedonlywhendatawithhigherresolution isnotavailable.

Grabsampleanalysesshouldbeperformed wheneverpossibletoconfirmordisprovemonitor'data, andtoprovideindication ofthenuclide-specific composition oftheeffluent.

Whengrabsampledataareavailable which,basedonventmonitordata,areindicative oftheperiodofelevatedrelease,doseratecalculations shouldbeperformed usingtheactualeffluentmix.Thedetermination ofcompliance statusshouldnotbebasedonmonitordataalonewhenitispossibletocollectandanalyzeaventsamplewhichwillberepresentative oftheperiodofelevatedrelease.OATRev.559 10.9Low-Level Radioactivit intheSewaeTreatment PlantLikeallsewageprocessing facilities, theSSESsewagetreatment plantcanundercertainconditions receivelowlevelsofradioactive materials.

Themostnotablescenarioiswhenindividuals whoworkon-sitehavebeensubjected tothemedicaladministration ofradiopharmaceuticals fordiagnostic ortherapeutic purposes.

Inthesecases,normalbiological elimination processes caneasilyresultinlevelsofradioactivity insewagetreatment plantsolutions andsuspensions whicharewithinthedetection capabilities oftheassociated samplingandanalysisprogram.Becausedisposalofsewagetreatment plantsludgebycontrolled dispersal onspecified tractsoflandisacommonpractice, thefollowing guidelines havebeenestablished:

a.At(sludgecollected inthesludgeholdingtankshouldbesampledandanalyzedpriortolanddisposaltoquantifyanyradioactivity

'resentabovenaturalbackground levels.b.Sludgecontaining nuclideswithshorthalf-lives, forexampleiodine-.131,shouldbecontained on-sitetopermitdecaytolessthandetectable levels.c.Whensludgeiscontaminated withnuclideswhichhavehalf-lives

'ufficiently longtomakehold-upfordecayimpractical, thefollowing optionsshouldbeconsidered:

1.Disposeofthesludgeaslowlevelradioactive waste.Rev.560 I'I"~v'i 2.Obtainaspecialpermitpursuanttotherequirements of10CFR20.2002.d.Thesewagetreatment plantliquideffluentshouldbesampledmonthlyforradioactivity.

Thiscanbeaccomplished bydrawing'a samplefromthechlorinecontactchamber.Rev.561 TABLE8SYSTEMSCLASSIFIED ASNOTANEFFLUENTPATHWAY(Page1of3)SYSTEMDESCRIPTION DomesticWaterRiverWaterMakeupIntakeCompressed AirScreensandScreenwash FireProtection WaterFireProtection CO2FireProtection HalonTurbineBuildingClosedCoolingWater'Building Drains:NONRADWaterPretreatment Condensate andRefuelWaterTransferLowPressureAirCondensate DeminsLubeOilTransfer/Purification CoolingTowerAcid/Chlorination Circulating WaterCondenser TubeCleaningFeedwater Extraction SteamFeedwater HeatersResidualHeatRemovalReactorCoreIsolation CoolingCoreSprayHighPressureCoolantInjection StandbyLiquidControlControlRodDrivesREFERENCE PPRLCalculation EC-ENVR-1 008Rev.562

TABLE8SYSTEMSCLASSIFIED ASNOTANEFFLUENTPATHWAY(Page2of3)SYSTEMDESCRIPTION Suppression PoolPrimaryContainment VacuumBreakersSuppression PoolCleanupReactorWaterCleanup'eactorPressureVesselReactorRecirculation SystemRadwasteChilledWaterSolidRadwaste/Cement SiloLRWCollection/Tb andCond.OuterAreaSumpsLRWProcessing/Radwaste Evaporator GaseousRadwasteRecombiner ClosedCoolingWaterNitrogenStorageHydrogenStorageSamplingStationsPostAccidentSamplingSystemBypassSteamMainSteamIsolation Valves/NuclearSteamSupplySystemShutoffAutomatic Depressurization SystemMSlVLeakageControlMoistureSeparators TurbineSteamSealsElectrohydraulic ControlStatorCoolingMainGenerator StormDrainsREFERENCE PP8LCalculation EC-ENVR-1008 Rev.563 TABLE8SYSTEMSCLASSIFIED ASNOTANEFFLUENTPATHWAY(Page3of3)SYSTEMDESCRIPTION MakeupDemineralizers FuelOilContainment Instrument GasControlStructure ChilledWaterTurbineBldg.ChilledWaterReactorBldg.ChilledWaterAuxiliary BoileisFuelPoolCoolingFuelPoolDemineralizers FuelPoolsTemporary SDHRSystemREFERENCE (1)PP8LCalculation EC-ENVR-1 008(7)SafetyEvaluation NL-95-001:

Refueling OutageDecayHeatRemovalandTie-lnoftheSDHRTemporary CoolingEquipment Rev.564 blII TABLE9SYSTEMSCLASSIFIED ASINSIGNIFICANT EFFLUENTPATHWAYSYSTEMDESCRIPTION H2SealOilCondensate/Refuel WaterStorageTankandBermMainTurbine/RFPT LubeOil/H2SealOilInstrument AirServiceAirTemporary LaundryFacilitySecondSort(DAWVolumeReduction)

FacilityLowLevelRadwasteHandlingFacilitySewageTreatment PlantREFERENCE (1),(8)(1)(8)(1),(8)(2)(3)(4)(9)(1)PPBLCalculation EC-ENVR-1008 (2)SafetyEvaluation NL-90-029:

Temporary IaundryFacility(3)SafetyEvaluation NL-89-002:

DryActiveWasteVolumeReduction System(4)SafetyEvaluation NL-92-007:.

Operation ofLLRWHFatSSES(8)MainTb/RFPTLubeOil,Instrument AirandServiceAiraredesignedtobeoperatedasnon-radioactive systems.Theyareclassified asinsignificant pathwaysbasedonsourcetermsandoffsitedoserateresultsforconsideration ofacontaminated sourceterm.(9)Sewagetreatment plant'isdesignedtobeoperatedasanon-radioactive system.Classification asaninsignificant effluentpathwayisinaccordance withSafetyEvaluation NL-95-015.

Rev.565 TABLE40SYSTEMSCLASSIFIED ASSIGNIFICANT fFFLUENTPATHWAYSYSTEMDESCRIPTION LiquidWasteManagement SystemsGaseousWasteManagement SystemsREFERENCE (5)(6)(5)SSESFSARChapter11.2(6)SSESFSARChapter11.3,oaRev.566

TABLE11SYSTEMSWITHNRCVEBULLETIN80-10APPLICABILITY SYSTEMNO.1618192735404852549399DDESCRIPTION ServiceWater(F/PHTXDischarge)

RHRServiceWaterInstrument AirServiceAirAuxiliary BoilersShutdownDecayHeatRemovalSystemBatchLubeOilTankFeedwater PumpTurbineLubeOilH2SealOilTankEmergency ServiceWaterMainTurbineLubeOilSewageTreatment PlantOATRev.567 41.0ODCMREVIEWANDREVISIONCONTROLTheSupervisor-Environmental Services-Nuclear shallensurethatatotalreviewoftheODCMisperformed duringeachevenwumbered year.Commentsshallbedocumented andrevisions initiated asappropriate.

Revisions totheODCMshallbeinitiated inaccordance withNEPM-QA-1011.

EachODCMpageshallbenumberedandprovidedwithanapprovalanddatebox.TheODCMTableofContentsshallpresentthecurrentrevisiondateforeachpagesothatanymanualholdercancheckmanualcompleteness basedonacurrentTableofContents.

AllODCMrevisions shallbereviewedbyPORCafterapprovalbytheManager-NuclearTechnology.

PORCreviewshallbeindicated byPORCchairperson ordesigneesignature onODCMcover.ODCMcopiesshallbeissuedinacontrolled fashionbySSESDocumentControlServices.

Thedistribution listshallbemaintained bySSESDocumentControlServices.

AnycommentsonODCMcontentsorproposedrevisions shouldbedirectedtotheSupervisor-Environmental Services-Nuclear.

Rev.568

APPENDIXBREVISIONS TOSSESSOLIDWASTEPROCESSCONTROLPROGRAIN(NDAP-QA-0646)

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'/Pp@//c$

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1 PROCEDURE COVERSHEET'NUCLEARDEPARTMENT PROCEDURE

~~rcS>SOLIDRADIOACTIVE WASTEPROCESSCONTROLPROGRAMNDAP-QA-064'6 Revision4Page1of63EFFECTIVE DATE:PERIODICREVIEMFREQUENCY:

PERIODICREVIEWDUEDATE:REVISEDPERIODICREVIEMDUEDATE'PROCEDURE TYPE:OAProgram(g)YES()NOPlant.Procedure

(~}YES()NOREVIEWMETHOD:()Alternate

()Expedited (Q)PORC()ERCPreparedbyRevi'ewed byRecommended SupervctionaUnManagerDate3-~~.9SDateApprovedbyPORCCommittee HeetingNo.ERCCottDateDateFORMNDAP-QA-0002-1, Rev.1,Page1of1IIIIHlslllllllIIIINlllIIIllIIIIlslflfllIIII lslllIIllliIlllllIlllSIl NDAP-OA-0646 Revision4'age2of63PROCEDURE REVISIONSUMMARYSOLIDRADIOACTIVE WASTEPROCESSCONTROLPROGRAM'Thefollowing changeswillnotreducetheoverallconformance ofthesolidified wasteproducttoexistingcriteriaforsolidwastes.1)Incorporated PCAF1-94-1330 revisingthePCPimplementing procedure matrixtoreflectactualprocedures inuseandchangedtherequirements fordisposalofradioactive waste'samplesafterpackagedradioactive wastehasbeeninitsdesignated storagearea.2),3)AddedSEGNRCapprovedTopicalReportSTD-P-05-Oll-P-A toContracted VendorServicestoreflectuseofSEGforwasteprocessing equipment, methodsandverification ofacceptable wasteformsfordewatering andsolidification.

AddedActivated Carbonasanewwastetypewhichisgenerated fromprocessing ofliquidwastesusingvendorprovideddemineralization services.

4).AddedtheSolidification/Dewatering/Services Vendormayperformtestsolidification anddetermination ofmixingratiosforsolidification performed offsite(vendorfacility) 5),6)AddedRadlok(SEG)typecontainers toHighIntegrity Container approvedforuselist.AddedSNHinventory requirements duringprocessing perSOOR94-581resolution.

7)AddedNRCTechnical PositiononConcentration Averaging andEncapsul'ation toRadioactive WasteAnalysisandClassification toensurethatradionuclide/concentrations areadequately distributed overthevolumeorweightofthewaste.

SECTION1.0PURPOSE2.0POLICY/DISCUSSION

4.0 RESPONSIBILITIES

TABLEOFCONTENTSNDAP-gA-0646 Revision4Page3of63PAGE,64.1EFFLUENTS MANAGEMENT SUPERVISOR 4.2SUPERVISOR

-OPERATIONS TECHNOLOGY 4.3.POMERPRODUCTION ENGINEER-EFFLUENTS MANAGEMENT 4.4HEALTHPHYSICIST

-EFFLUENTS MANAGEMENT 4.5RADMASTESUPERVISOR 4.6CHEMISTRY SUPERVISOR 4.7HPFOREHAN-EFFLUENTS MANAGEMENT 4.8MANAGER-NUCLEAR ASSESSMENT SERVICES4.9AUXILIARY SYSTEHSOPERATOR4.10SOLIDIFICATION/DEWATERING/SERVICES VENDOR4.11HANAGER-NUCLEARPROCUREMENT 4.12HANAGER-NUCLEARSYSTEMSENGINEERING 4.13MANAGER-NUCLEARMAINTENANCE 4.14LICENSING SUPERVISOR 4.15MANAGER-NUCLEARTRAINING4.16HANAGER-NUCLEARSECURITY5.0DEFINITIONS 101012131313141414151515 NDAP-gA-0646 Revision4Page4of63SECTION6.0PROCEDURE TABLEOFCONTENTSContinued PAGE20.6.1CONTRACTED VENDORSERVICES6.2WASTETYPES6.3RADIOACTIVE MASTEANALYSISANDCLASSIFICATION 6.4TESTING/TREATMENT OFSOLIDIFIED RADMASTEFORCOMBUSTIBLE GASES6.5RADIOACTIVE WASTESOLIDIFICATION 6.6RADIOACTIVE WASTEDEWATERING 6.7HIGHINTEGRITY CONTAINERS (HIC)6.8IRRADIATED HARDMAREPROCESSING ANDDEWATERING 6.9CONTAINER INSPECTIONS 6.10WASTECONTAINER SPACEUTILIZATION 6.11STORAGEOFPACKAGEDRADIOACTIVE WASTE6.12TRANSPORTATION, SHIPPINGANDDISPOSALREGULATIONS 6.13SHIPPINGOFRADIOACTIVE

.WASTE6.14SHIPMENTCONFIRMATION 6.15CHANGESTOTHESOLIDRADIOACTIVE MASTEPROCESSCONTROLPROGRAM6.16EVALUATION OFPROCESSOROPERATIONAL CHANGES6.17REPORTING OFHISHAPSINVOLVING LOWLEVELWASTEFORNS6.18PCPIHPLEHENTING PROCEDURES 7.0RECORDS2021'73030404246474748515151525354 NDAP-0A-0646 Revision4Page5of63ATTACHMENT ATTACHMENTS PAGEASolidification RecordSheetBDewatering RecordSheetCSusquehanna Guaranteed Solidified/Dewatered WasteVolumeRecordDPCPImplementing Procedure MatrixEMaterials notCompatible withPolyethylene Containers 55566063 NDAP-QA-0646 Revision4Page6of631.0PURPOSEProvideadministrative control,guidanceandrecordsfortheprocessing, packaging, transportation, anddisposalofradioactive waste.Thisprocedure istheProcessControlProgramrequiredbySSESTechnical Specifications.

'2.0~LICIUKMThisprocedure isapplicable toLowLevelRadwaste(LLRW)generated asaresultoftheoperation oftheSusquehanna SteamElectricStation(SSES).Thewastestreamsincludesolidandliquidwaste'asdefinedintheFSAR,butdonotincludespentfuelorgreaterthanClassCwaste.Efficient generation andprocessing ofradioactive wasteisveryimportant totheoveralloperation ofSSES.Animportant objective withrespecttoradioactive wastegeneration istominimizethevolumeofwastegenerated.

Theprocessing oflargevolumesofwastecanresultintheinability todisposeoforstore'allwastepackaged, thesignificant increased costsassociated withincreased wastegeneration, andthe-potential toover-burden theprocessing systemanddegradeitslongtermreliability.

TheProcessControlProgramdescribes theenvelopewithinwhichprocessing andpackaging ofradioactive wasteisaccomplished toprovidereasonable assurance ofcompliance.

withLow-Level Radwasteregulations andrequirements.

Th'isprocedure isapplicable toSSESinstalled systems,temporary systemsandequipment providedbyvendorsforprocessing, packaging, transportation, anddisposalofapplicable wasteforms.

3.0REFERENCES

3.149CFR100-l77,Transportation 3.210CFR20,Standards forProtection AgainstRadiation 3.310CFR61,Licensing Requirement forLar"DisposalofRadioactive'aste A3.410CFR71,Packaging andTransportation ofRadioactive Material3.540CFR261, Identification andListingofHazardous Waste3.63.7SSESTechnical Specifications Section3/4.11.3,SolidRadwasteSystemSSESTechnical Specifications Section6.13,ProcessControlProgram(PCP) he'i NDAP-0A-0646 Revision4Page7of633.83.93.103.113.123.133.143.15NUREG0800,StandardReviewPlan11.4SolidWasteManagement SystemsTechnical PositiononWasteFormRev.1,1991Technical PositiononRadioactive WasteClassification, Rev.0,1983Technical PositiononConcentration Averaging andEncapsulation; Rev.0,1995Regulatory Guide1.21,Measuring, Evaluating andReporting Radioactive MaterialinSolidWastesandReleaseofRadioactive MaterialinLiquidandGaseousEffluents fromLightWaterCooledNuclearPowerPlantsRegulatory Guide1.143,DesignGuidanceofSolidWasteManagement'ystems Regulatory Guide7.1,Administrative GuideforPackaging andTransporting Radioactive MaterialANSI/ANS40.35,VolumeReduction ofLowLevelRadioactive Waste3.16ANSI/ANS40.37, MobileRadioactive WasteProcessing Systems3.173.183.193.20ANSI/ANS55.1,SolidRadioactive Wast'eProcessing SystemforLightWaterCooledReactorPl.antPacificNuclearDewatering SystemTopicalReportNo.TP-02-P-A, Rev.3PacificNuclearSolidification ProcessControlProcedure No.PT-51-WS, Rev.40Scientific EcologyGroupMobileIncontainer Dewatering andSolidification System(MDSS)TopicalReportNo.STD-R-05-011-P-A; Rev.23.21DisposalSiteCriteriaforBarnwell, S,C.3.22DHEC-HIC-PL-001 SouthCarolinaCertificate ofCompliance forCNSIHighIntegrity Containers 3.23DHEC-HIC-P0-006, SouthCarolinaCertificate ofCompliance forCNSIOverpackHighIntegrity Containers 3.24DHEC-HIC-PL-012, SouthCarolinaCertificate ofCompliance forVectraTechnologies, Inc.HighIntegrity Container I

(")()()4.0NDAP-gA-0646 Revision4Page8of633.25DHEC-HIC-PL-005, SouthCarolinaCertificate ofCompliance forScientific EcologyGroup,Inc.HighIntegrity Containers 3.26DHEC-HIC-PL-017, SouthCarolinaCertificate ofCompliance forScientific EcologyGroup,Inc.HighIntegrity Containers 3.27PLA-1237, ProcessControlProgram,August17,19823.28ReviewofProcessControlProgramforSusquehanna, UnitI,Youngblood toCurtis,September 30,19823.29SafetyEvaluation NL-93-008, SolidRadwasteWasteProcessing ServicesUtilizing PacificNuclearProcessing System3.30IEBulletin79-19,Packaging ofLowLevelRadioactive WasteforTransportation andBurial3.31NRCInformation.

NoticeNo.90-50,Minimization ofMethaneGasGeneration inPlantSystemsandRadwasteShippingContainers.

3.32GenericLetter91-02,Reporting MishapsInvolving LLWFormsPreparedforDisposal3.33SOOR-1-90-148, BarnwellReceivedContainer Pressurized withFlammable Gas3.34SOOR1-90-172, Incorrect SamplingMethodUsedonResinLiner3.35SOOR1-91-322, DoseRatesonContainer HigherThanExpected3.36SOOR94-581,SpentTIPFoundUnexpectedly inTIPRoom.tRESPONSIBILITIES4.1'ffluents Management Supervisor responsibilities:

4.1.14.1.24.1.3Developing andimplementing programsandprocedures forradioactive wasteprocessing, packaging, transportation anddisposal.

Maintaining theoverallradwasteprogramtoensurecompliance withapplicable radiological andshippingregulations.

Ensuringpersonnel whoperformsupportactivities suchasprocessing, packaging, andtransportation oflow'evelradioactive wasteareavailable andmeetallqualifications andtrainingrequiredbySSESprocedures..

NDAP-QA-0646 Revision4Page9of63Collecting, maintaining, reviewing andsubmitting accuratedata/information relatedtowastestreamquantityandnuclidecomposition forinclusion intoAnnualRadioactive EffluentReleaseReportandStateDER-BRP'Quarterly Report.4.2Supervisor

-Operations Technology responsibilities:

Providing technical assistance toEffluents Management personnel.

Thisincludesinterpretations ofstate,federal,anddisposalfacilityregulations regarding new,imminent, orproposedregulatory changesgoverning processing, packaging, transportation, anddisposal.

4.2.24.2.3Maintaining acurrentcopyoflocal,state,federalanddisposalfacilityregulations pertaining todisposalandtransportation oflowlevelradioactive waste.Coordinating thesubmittal oftheAnnualRadioactive EffluentReleaseReportaspertheSSESTechnical Specifications.

4.3PowerProduction Engineer-Effluents Hanagement responsibilities:

Ensureprocedures areadequatetoprovideforpropersolidification anddewatering ofwaste.4.3.24.3.34.3.44.3.5Ensuretestdataorrationale isavailable tojustifyapplicable solidification anddewatering functions ofeachwastetype,oranycombinations, toaddressdisposalandregulatory agencies'equirements.

Evaluateservicesprovidedbyvariousvendorstoensurecontracted solidification anddewatering operations areperformed inthemostefficient andeconomical method,asrequiredbytheapplicable regulatory agencies.

PerformthedutiesofRadwasteSupervisor asspecified inthisprocedure inhisabsence.Definewastestreamsbasedongenerator, filtration mediaandmeansofprocessing.

'P NDAP-gA-0646 Revision4Page10of634.3.6Collecting, reviewing andsubmitting datarelatedtothereporting ofmishapsandresultsofPCPsurveillance specimenexaminations toapplicable regulatory agencies.

4.4HealthPhysicist

-Effluents Management responsibilities:

4.4.14.4.24.4.34.4.44.4.5Maintainasamplingandarialysis programtoensurelOCFR61compliance.

Ensureprocedures areadequatetoprovideforproperpackaging andshipmentofwastetoensurecompliance withallapplicable regulations.

Evaluateservicesprovidedbyvariousvendorstoensurecontracted wastepackaging, processing, andtransportation servicesareperformed inthemostefficient andeconomical method,asrequiredbyapplicable regulatory agencies.

PerformthedutiesofHPForeman-Effluents Management asspecified inthisprocedure inhisabsence.Coordinate radioactive materialevaluation ofproductacceptability fordisposalatspecificdisposalfacilities.

4.5RadwasteSupervisor responsibilities:

4.5.14.5.24.5.34.5.4'nsure Solidification/Dewatering Equipment isoperatedinaccordance withapprovedoperating procedure, incl.uding vendorsuppliedequipment.

Ensureappropriate wastesolidification and.dewatering records'are generated.

Interface withstationsupportgroupstoensureproperimplementation ofprocesscontrolprograms.

Providedirection tocontractor personnel involvedinsolidwasteprocessing activities including:

a~b.Ensuringtestdataisavailable tojustifyspecificprocessing techniques.

Ensuringapplicable vendorprocedures andrevisions areincorporated intoapplicable plantprocedure andapprovedbyPORC.

NDAP-gA-0646 Revision4Pagellof63c.Coordinating pre-processing andpost-processing treatment activities.

d.Evaluating servicesprovidedtoensureefficient andeconomical methodsareused.4.5.54.5.6EnsureSolidification andDewatering operations arecarriedoutinanALARAmanner.Interface withHPForeman-Effluents management forlinerandcaskselection forsolidwasteshippingactivities.

4.5.74.5.84.5.94.5.104.5.114.5.12Ensurepropermarkingofcontainers priortofilling.Ensuresolidification/dewatering personnel areadequately trainedperNTP-gA-42.6.

Estimateclassification ofwasteforcontainer selection andprocessing method.Ensurethat'waste streamsloadedintoHighIntegrity Containers aresampledforradionuclide andevaluated forchemicalcompatibility applicable totheuseofHighIntegrity Containers.

Ensureproperinspections anddocumentation arecompletepriortouseofaHighIntegrity Container andensurethatcontainer isproperlyuseduptothepointoftransfertoHPForeman-Effluents Nanagement.

CompleteandprocessHighIntegrity Container UserCertification Statement toensurethecontainer isusedproperly.

4.6Chemistry Supervisor responsibilities:

4.6.14.6.24.6.34.6.4Performrequiredsamplepreparation andanalysisinaccordance withapprovedchemistry procedures, Performtestsolidification ifrequired.

Storetestsolidification billetifrequired.

Providedensityofinitialandfinalwasteform.Providetheisotopicmixandconcentration ofisotopesdetectedinthematerialsampledforsolidification ordewatering.

NDAP-gA-0646 Revision4Page12of634.6.54.6.6CompleteChemistry portionoftheSolidification andDewatering Records.Ensurepersonnel areadequately trainedperNTP-(A-41.2.

4.6.7-Providechemicalanalysisand/ortreatment supportasnecessary foruseofHighIntegrity

.Containers andliners.E4.7HPForeman-EffluentsManagement responsibilities:

4.7.14.7.2Interface withRadwasteSupervisor forlinerandcaskselection andscheduling forsolidwasteshippingactivities.

Complete, process,and,fileradioactive wasteshippingdocumentation.

4.7.3Storageofpackagedradioactive wastewithintheradwastefacilities.

4.7.44.7.54.7.64.7.74.7.8Determine wasteclassification anddescription ofsolidified, dewatered, andotherpackagedwaste.Finaldisposition ofsolidified, dewatered andotherpackagedwaste.EnsuresSSESisaregistered userofapplicable HighIntegrity Containers atspecificdisposalfacilities.

EnsuresHPpersonnel involvedwithradioactive wastehandl.ing havereceivedRadwasteWorkertrainingperNTP-(A-42.6.

Evaluatevendorservicesprovidedtoensureefficient andeconomical methodsareused.4.7.94.7.10CompleteandprocessCert:"cationStatement forDisposalofHighIntegrity Containers asrequiredbyapplicable regulatory agencies.

ProcessandpackageCartridge Filters,DryActiveWaste,solidsealedsourcesandothernonprocesswastes.4.7.11Collection ofDAWandnon-process waste(IOCFR61) samples.

NDAP-gA-0646 Revision4Page13of63'.8Hanager-Nuclear Assessment Servicesresponsibilities:

4.8.14.8.24.8.34.8.4Performperiodicauditofimplementation ofthisprogramandreviewofradwasteservicevendor'sgAPrograms.

Inspection ofRadwaste,Containers asrequiredbyapplicable procedures.

Ensureprocesscontrolsareadheredtobyinspection oftestsolidification, wastevolumes,solidification agentadditions, productacceptability checks,dewatering processsequence/acceptance criteriaandrecordsreview.Inspection ofpackaging, storage,andshippingactivities, asrequiredbyapplicabl.e procedures.

4.9Auxiliary SystemsOperatorisresponsible foroperating theplant.solidandliquidradwasteequipment inaccordance withapprovedoperating procedures asdirectedbytheRadwasteSupervisor andAssistant UnitSupervisor.

4.10Solidification/Dewatering/Services Vendorresponsibilities:

.Providesolidification, dewatering and/orvolumereduction servicesinaccordance withavalidcontractforsaidservices.

4.10.24.10.34.10.44.10.5Providetestdataormakedataavailable forPP8Lreviewduringvendorauditstodemonstrate thattheirservicesandequipment meettheapplicable regulatory anddisposalfacilitylimitations fortheservicetheyareproviding.

Providetrainingdocumentation todemonstrate thatthepersonnel beingprovided, toconducttheapplicable

• service,areinfacttrainedandknowledgeable intheapplicable services.

Provideprocedures thatareorcanbeplacedintotheSSESprocedure formatfortheservicesbeingprovided.

EnsureanapprovedgualityAssurance Programexiststhatcoverstheservicesbeingprovided.

ThevendorshallworkwithintheSSESgualityAssurance Programwhenapplicable.

'C' NOAP-OA-0646 Revision4Page14of634.10.64.10.7Completeapplicable sectionsofSolidification andDewatering Recordsrequiredforeachcontainer processed.

Ensurepre-qual'ification testdataforeachwasteformshallbesubmitted totheNuclearRegulatory Commission.

'4.10.84.10.94.10.104.11Hanager-4.11.14.11.2Provideadescription oftheequipment/process that;isusedinprocessing waste.Obtainwastesamplesfromprocessing equipment inaccordance withapprovedoperating

.procedures.

Performallpreandposttreatment activities asdetermined byRadwasteSupervisor.

NuclearProcurement responsibilities:

HEnsureHighIntegrity Containers arenotexposedtoultravioletlight(sunlight).

Ensurepropermaterialcertification iscompletepriortoissuanceofHighIntegrity Containers toplantforuse.4.11.3Receiptinspection ofHighIntegrity Containers anddocumentreviewtoensureconformance.

4.11.4EnsureCertificate ofCompliance (CofC)isreceivedwithHighIntegrity Container.

4.12Manager-NuclearSystemsEngineering isresponsible forproviding engineering supportasrequiredforoperation ofassignedradwastesystemsandequipment.

4.13Manager-NuclearMaintenance responsibilities:

4.13.14.13.2Calibration andmaintenance ofapplicable plantequipment inRadwasteProcessing Systems.Providemaintenance personnel tosupportprocessing, packaging andtransportation oflowlevelradioactive waste.4.14Licensing 4.14.1Supervisorresponsibi1 ities:Submitting transportation caskuserregistration requeststo,NRCperlOCFR71.12.

NDAP-gA-0646 Revision4Page15of634.14.24.14.3'Submitting totheNRCtheAnnualRadioactive EffluentReleaseReport.Coordinating andsubmitting totheNRC'thereportsrequiredasaresult.ofCondition Report(CR)events,investigations, andresolutions.

4.15Manager-NuclearTrainingresponsibilities:

4.15.1Prov'd'ntra'niadiigingnretraininginapplicable regulatory requirements topersonnel directlyinvolvedintransfer, processing, packaging, storage,andtransport ofradioactive waste.4.15.2Maintaining arecordoftraining, attendees, andsubjectmaterialforallLowLevelRadioactive Mastetraining.

4.16Manager-NuclearSecurityisresponsible fornotifying appropriate lawenforcement a'gencies intheeventoflostradioactive materialshipments.

5.0 DEFINITIONS

5.1APPROYEDCONTAINERS:

Approvedmeansapprovalissuedorrecognized bytheNRCforuseinshipmentofradioactive material.

5.25.3BATCH:Thetotalvolumeofwastecontained inaliner,isolated-wastemixingtank-spentresintank-concentrates tankor-phaseseparator thathasbeensampledforsolidification/dewatering.

BILLSOFLADING:Shippingpapersormanifests servingasimilarpurposeandcontaining theinformation requiredby49CFR172.202,203,and204.5.4CARRIER:Meansapersonengagedinthetransportation ofpassengers orproperty.

(10CFR71.4) 5.5CERTIFICATE OFCOMPLIANCE:

Licenserequirements established bytheNuclearRegulatory Commission for.theuseofapprovedRadioactive MaterialShippingContainers.

5.6'CHELATING AGENT:Achemicalwhichcombineswithametalsoastoformaringstructure heldbycoordination bonds.

NDAP-gA-0646 Revision4Page16.of635.75.85.9CHEMICALFORM:ThechemicalcontentoftheRadioactive Materialbeingshipped.CLOSEDTRANSPORT VEHICLE:Avehicleequippedwithasecurelyattachedexteriorenclosure, whichduringnormaltransport, restricts theaccessofunauthorized personstothecargospace.(49CFR173-403[C])

COMPOSITE SAMPLE:Amixtureofsamplescollected representing conditions attimeofsampling, fromthesamesamplingpoint,atdifferent times.5.10CONSIGNEE:

Theindividual ororganization towhomtheshipmentisconsigned orintended.

5.11CURINGTIME:Thetimeallowedforthesolidified producttosetpriortoitsevaluation forproductacceptability.

5.125.135.145.15'5.16DECAY'EAT:

Theheatproducedbyradioactive decay,usuallyexpressed inWattsorBTU/hr,butcanberelatedtoCurieContent.DEWATERED:

TheremovaloffreeliquidfromsolidmaterialtoapointwherelessthanIXforHIC'sandlessthan0.5Xforsteellinersbywastevolumeremainsasrequiredbythedisposalfacilitylicense.EXCLUSIVE USEVEHICLE(a/k/a:SoleUseorFullLoad):Shipmentfromasingleconsignor havingtheexclusive useofatransport vehicleandforwhichallinitial,intermediate.

andfinalloadingandunloading iscarriedoutby,orundertheairection oftheconsignor, consignee, orhisdesignated agent.(49CFR173.403[i])

FREELIQUID:Liquidwhichisstillvisibleaftersolidification ordewatering iscomplete, orisdrainable fromthelowpointofapunctured container.

1HAZARDOUS MATERIAL-Asubstance ormaterial, including ahazardous substance whichhasbeendetermined bytheSecretary ofTransportation tobecapableofposingathreattohealth,safety,andpropertywhentransported incommerce, andwhichhasbeensodesignated.

Thetermincludeshazardous substances, hazardous wastes,marinepollutants, andelevatedtemperature materials asdefinedin49CFR171.8, materials designated ashazardous undertheprovisions of49CFR172F101and172.102,andmaterials thatmeetthedefiningcriteriaforhazardclassesanddivisions in49CFR173.

.NDAP-gA-0646 Revision4Page17of635.17=5.18HAZARDOUS WASTE:Wastewhichcontainsmateriallistedin40CFR261,SubpartDand/orexhibitsoneormoreofthefourcharacteristics citedin40CFR261,SubpartC,andisnotexcludedfromregulation under40CFR261,SubpartA.HazmatEmployeemeansapersonwhoisemployedbyaHazmatEmployerwhoduringthecourseofemployment:

5.18.1Loads,unloadsorhandleshazardous materials.

5.18.2Prepareshazardous materials fortransportation.

5.18.35.18.4Modifies, marks,orotherwise represents containers, drums,orpackagings asqualified foruseintransport ofhazardous materials.

Isresponsible forsafetyoftransporting h'azardous material.

5.195.205.215.225.235.245.25HIGHINTEGRITY CONTAINER (HIC):Adisposalsiteapprovedcontainer thathasanexpectedlifeof300yearsandprovidesthestructural stability tbmeetdisposalrequirements.

HIGHWAYROUTECONTROLLED QUANTITY:

Aquantity',

theaggregate radioactivity ofwhichexceedsthatspecified in(49CFR173.403[1]).

ISOTOPICANALYSIS:

Theidentification oftheisotopicelements.involvedinasampleofRadioactive Material.

LABELING:

Labelsappliedtoacontainer denotingthecontentsofthecontainer anddegreeofhazardassociated withthecontainers.

Thelabelsare.identified astheWhiteIlabel,theYellowII,andYellowIIIlabel.AlabelstatingRadioactive

-LSAcanalsobeappliedtoacontainer whenappropriate.

(49CFR172,.SubpartE)LIMITEDQUANTITYOFRADIOACTIVE MATERIAL:

Meansaquantityofradioactive materialnotexceeding thematerialpackagelimitsspecified in49CFR172.423,andwhichconformswithrequirements specified in49CFR173.421.(49CFR173.403[m])

LINER:Steelcontainer inwhichdewatered orsolidification productisdeposited.

LOWSPECIFICACTIVITY:

Materialinwhichtheactivityisessentially uniformly distributed andinwhichtheestimated averageconcentration pergramofcontentsdoesnotexceedthespecification asstatedin49CFR173.403(n).

NDAP-gA-0646 Revision4Page'18of635.265.275.285.295.305.315.325.335.345.355.36LOWLEVELRADIOACTIVE WASTE(LLRW):Radioactive wastegenerated asaresultofoperation ofSSES,excluding spentfuelorbyproductmaterial, isclassified bytheNRCaslow-level

~radioactive waste.LLRWdoesnotinclude"greaterthanclassC"waste.MIXINGRATIO:Theratioofwastetocementandadditives requiredforsatisfactory solidification.

MIXINGRECIPE:Theamountofwaste,cementandadditives mixedtosolidifywaste.MIXEDWASTE:Amixtureoflowlevelradioactive andhazardous waste.NORMALFORMRADIOACTIVE MATERIALS:

Meansradioactive materials whichdonotmeettherequirements ofSpecialFormRadioactive Materials (49CFR173.403[s]).

PLACARDING:

Alabelaffixed'to allfoursidesofthetransport vehicledenoting'thepresenceandlevelofRadioactive materialonthevehicle.(49CFR172,SubpartF)PROCESSCONTROLPROGRAM(PCP):Programwhichcontainsthesampling,

analysis, andformulation determination bywhichsolidification ofradioactive wastesfromliquidsystemsisassured.RADIOACTIVE MATERIAL:

Forpurposesoftransportation only,materialinwhichtheactivityisessentially uniformly distributed andtheestimated specificactivityexceeds0.002microcuries pergramofmaterial.

(49CFR173.403[y]

and[aa])RADWASTEWORKER:AHazmatEmployeeinvolvedwiththe.collection',

packaging, andtransportation ofradioactive waste.SEALEDSOURCES:Anyby-product materialthatisencasedinacapsuledesignedtopreventleakageoscapeofby-product material.

SOLIDIFICATION:

Aconversion ofradioactive materials fromliquidandsolidsystemstoahomogeneous (uniformly distributed) monolithic, immobilized solidwithdefinitevolumeandshape,boundedbyastablesurfaceofdistinctoutlineonallsides(freestanding).

I NDAP-gA-0646 Revision4Page19of635.375.385.395.405.415.425.435.44SOLIDIFIED RADWASTE:

Wetwastewhichissolidified (e.g.evaporator concentrates, sludge),meetsthefreeliquidcriteria, andsatisfies applicable transportation anddisposalsite.requirements.

Dewatered resinsorfiltersludgesatisfying the,twolattercriteriashallalsobedefinedassolidified radwaste.

SPECIALFORMRADIOACTIVE MATERIALS:

Radioactive.

materialthatiseitherasinglepiece,oriscontained inasealedcapsule,,that canbeopenedonlybedestroying thecapsuleandmeetstheadditional requirements specified in49CFRPart173.403(z).

STABLEANDUNSTABLEWASTEFORMS:Shallbedefinedasstatedin10CFRPart 61andothersupporting regulatory documents.

TESTSOLIDIFICATION:

Themixingofwaste(s)andsolidification agentsinthelaboratory tosupportselection ofmixingratiosand,provideinsurance forfinalproductacceptability.

TRANSPORT INDEX(TI):Thedimensionless numberplacedonthelabelofapackagetodesignate thedegreeofcontroltobeexercised bythecarrierduringtransportation.

Thetransport indexwillbedetermined inaccordance with49CFR173.403(bb).

TYPE"A"PACKAGING:

Packaging whichisdesignedinaccordance withthegeneralpackaging, requirements of49CFR173.24,ahdwhichisadequatetopreventthelossordispersal oftheradioactive

contents, andtoretaintheefficiency ofitsradiation shielding properties ifthepackageissubjected tothetestdescribed in49CFR173.'465or173.466,asappropriate.

(49CFR173.403[gg])

TYPE"A"QUANTITYRADIOACTIVE MATERIAL:

Thatmaterialwhichmaybetransported inType"A"packaging.

(49CFR173.431[a])

TYPE"B"PACKAGING:

Packaging whichmeetsthestandards forType"A"Packaging, andinaddition, meetsthestandards forthehypothetical accidentconditions setforthin10CFR71.(49CFR173.403[hh])

5.45'YPE"B"QUANTITYRADIOACTIVE MATERIAL:

Thatmaterialwhichmaybetransported inType"B"packaging.

(49CFR173.431[b])

5.465.47WASTESTREAM:Aby-product ofaprocesssystemorcomponent withuniquecharacteristics andmaintained separatefromotherwastestreams.WASTETYPE:Specificcontentsofalinerortankwhichmaycontainoneormultiplewastestreams,thecategoryofwastesuitableforaparticular meansofprocessing"..

'II NDAP-QA-0646 Revision4Page20of635.48WASTEPRE-CONDITIONING:

Thephysicalorchemicaladjustment ofthewastetobringitwithinanestablished envelopetoassuresolidification.

6.0 PROCEDURE

6.1CONTRACTED VENDORSERVICES6.1.16.1.26.1.36.1.4F1.56.1.6Solidified radwasteprocessing servicesareprovidedbyVectra,Inc.forwastetypesincludedinthisProcessControlProgram.NRCapprovedTopicalReportTP-'02-P-A, describes, VectraInc.wasteprocessing equipment, methodsandverification ofacceptable wasteformsfordewatering.

VectraInc.Solidification ProcessControlProcedure PT-51-WS, describes wasteprocessing equipment, methodsandverification ofacceptable wasteformsforsolidification.

Thisprocedure doesnotprovidestability pertheBranchTechnical PositiononWasteForm,Rev.l.Volumereduction servicesareprovidedbyScientific EcologyGroup(SEG)forwastetypesincludedintheProcessControlProgram.NRCapprovedTopicalReportSTD-P-05-011-P-A, aescr>bes Scientific EcoplogyGroup(SEG)wasteprocessing equipment, methodsandverification ofacceptable was'teformsfordewatering andsolidification.

Selectedsolidified wasteformshavebeenapprovedtoprovidestability pertheBranchTechnical PositiononWasteForm,Rev..1.Othercontracted vendorserviceswhicharerequired.forsolidification, dewatering andvolumereduction servicesshallbeevaluated totherequirements statedinthisProcessControlProgramonacasebycasebasis.

NDAP-gA-0646 Revision4Page21of636.2WASTETYPESThefollowing wastetypesshallbeprocessed inaccordance withthisprocedure orincombinations asdefined.Thewasteshouldbedewatered wheneverpossibletominimizedisposalvolume.6.2.1Evaporator Concentrates a~Thefollowing areconcentrated withtheRadw'aste Evaporators andareconsidered Evaporator Concentrates wastestream:(1)Condensate Demineralizer regeneration effluentb.C.d.(2)DeconShopdrains(3)Chemistry Laboratory sinkdrains(4)Auxil'iary BoilerblowdowneffluentTheconstituents ofthiswastestream.may includethefollowing:

(1)Tri-Sodium Phosphate (2)SodiumSulfate(3)Phosphoric Acid(4)SulfuricAcid(5)SodiumHydroxide (6)Decontamination solutions

(?)Negligible amountsofreagentchemicals usedforchemistry

.analysis Evaporator Concentrates intherangeof0-24weightpercentsodiumsulfate(equivalent) shallbesolidified forfinaldisposal.

Evaporator Concentrates shallnotbemixedwithanyotherwastetypeinfinalprocessing.

NDAP-gA-0646 Revision4Page22of63HixedSolidsa.Thefollowing processwastestreamsarecollected eitherinWasteHixTanks,WasteSludgePhaseSeparator ortransferred directlytoaliner/High Integrity Container andareconsidered HixedSolids:b.(1)LRWFilterHedia.anddrainliquid(2)SumpSludge(3)Ultrasonic ResinCleanerWaste'(URC Waste)Theconstituents ofthesewastestreamsmayincludethefollowing:

(1)Diatomaceous Earth(2)PowderedResins(3)Fibrousmaterial(4)Carbonmaterial.(5).Corrosion products(6)Varioussolidsanddirtinsmallconcentrations c~HixedSolidsmaybesolidified ordewatered forfinal.disposal.

d.Eachwastestreamshouldbeprocessed separately.

RWCUFilterHediaa.TheReactorWaterCleanupSystemandFuelPoolCoolingandCleanupSystemfilter/deminer alizerwastearecollected intheRWCUPhaseSeparator andshouldbeallowedtodecayfor60days.Thiswastestreamisconsidered RWCU.FilterMedia.'.Thconstituents ofthiswastestreammayincludeanionandcationpowderedresin,corrosion andcontaminants removedfromtheprimarycoolant.

401ft NDAP-gA-0646 Revision4Page23of63C.RWCUFilterMediashallbedewatered inHighIntegrity Containers.

Ifthiswastemustbesolidified, Technical Specification 3/4.11.3actionstatement mustbeperformed.

Condensate/Radwaste/Atmospheric Demineralizer BeadResina~ResinsfromtheCondensate Demineralizers, LiquidRadwasteOemineralizer andvendorprovideddemineralization arecollected intheSpentResinTankortransferred directlytoaliner/High Integrity Container.

Thi'sisconsidered tobeCondensate/Radwaste/Atmospheric Demineralizer BeadResin.b.C.Theconstituents ofthiswastestreammayincludevarioustypesofanion,cation,mixedbeadresinandcorrosion andcontaminates removedfromliquidwastestreams.BeadResinmaybeusedtodemineralize LiquidWasteineithersteel.linersorHighIntegrity Containers.

d.e.Condensate Demineralizer beadresinshouldbeultrasonically cleanedpriortocollection intheSpentResinTank.BeadResinmaybesolidified ordewatered forfinaldisposal.

BeadResinmayalsobeprocessed byvolumereduction methodswhichincludedrying,incineration, compaction, useasfillmaterials orotherevaluated method(s) onacasebycasebasis.Cartridge FiltersCartridge Filterwastetypeconsistsofthefollowing wastestreamsandconstituents:

(I)CRDFilters-CRDorotherfiltersandsmallun-irradiated primarysystemequipment suchasvalves,CRDliftpumpfilters,RinseTankfiltersandothermetalcomponents.

NDAP-gA-0646 Revision4Page24of63b.(2)RWCUSepta-SeptafromRWCUFilterDemineralizer including septafromFuelPoolCleanupFilterDemineralizer.

(3)RadwasteFilters-including degasifier filtersandotherfiberorpaperfiltersotherthanprimarysystem.(4)Underwater VacuumFilters-non-process'ilters generated fromwetcleaningactivities.

Cartridge Filtersmaybeprocessed bythefollowing methods:1(I)Emplacement inacementmatrixinasteel.drum/liner orinaHighIntegrity Container.

C.d.(2)Driedtoapointwherenofreeliquidisvisible.Absorbent materialmaybeincludedtoabsorbunintentional andincidental amountsofliquids.(3)Dewatered ifdryingisimpractical.

(4)Incineration orothervolumereduction methods.Cartridge Filterstobesolidified forfinaldisposalshallnotbemixedwithanyotherwastetype.Eachcartridge filterwastestreamshouldbepackagedseparately unlessanalyzedpriortopackaging inaccordance withtherequirements of.thisprocedure.

Irradiated Hardware'a~Irradiated hardwareisneutronactivated metalremovedfromtheinternalareaofthereactorpressurevessel.Thiswastestreamisconsidered Irradiated Hardware.

'I NDAP-gA"0646 Revision4Page25of63b.Theconstituents ofthiswastestreammayincludecontrolrodblades,LPRHS's,IRH's,'IP'sandcomponents expendedduringhardwareprocessing andpackag'ing acti.vities.

Startupsourcesmayalsobeprocessed aspartofthis'astestream.c.Irradiated hardwareispackagedinsteellinersfordisposal.

d.LiquidshallbedrainedtoensurefreeliquidAcceptance Criteriaaremet.e.Irradiated hardwareshallnotbemixedwithanyotherwastetypeinfinalprocessing.

DryActiveWaste(DAM)a.DryActiveWasteisawastestream.b.Theconstituents ofthiswastestreamconsistofcontaminated paper,plastic,wood,metalandotherdiscarded material.

C.DryActiveWasteshallbeprocessed byvolumereduction methodswhichmayincludeincineration, compaction, decontamination andmetalmelting.d.Ataminimum,DAWshallbepackagedinstrong-tightcontainers fordisposal.

LiquidOilWasteorPetroleum BasedHaterials

.a.b.Theconstituents ofthiswastestreammayincludeturbinelubricating oil,EHCfluidandotherpetroleum basedmaterials.

Contaminated LiquidOilWastegenerated atthefacilityshouldbeprocessed byadecontamination system,solidified forfinaldisposal, volumereducedbyincineration, orotheracceptable methods.

e NDAP-gA-0646 Revision4Page26of63C.LiquidOilWasteatconcentrations IXandgreatermaybesolidified providedthefollowing areadheredto:(I)Anemulsification ageritisaddedatrequiredconcentrations.

(2)TheLinerisNOTSHIPPEDtoa.disposal

.facilitywithoutpriordisposalfacilityapproval.

SolidSealedSourcesa.SolidSealedSourcesrequiring disposalshallbe.packagedfordisposalasrequested byHealthPhysicsSupervision.

b.Methodofdisposalisdependent onwasteclassoftheSolidSealedSourceanddisposalfacilityrequirements.

c.Acceptable methodsofdisposalinclude:~(I)Placement withinacontainer consisting ofanotherwastetypeprovided:

(a)Thesourcecontainsisotopics alreadyinthewaste.(b)Thesourceactivityissignificantly

~lessthanthewasteactivity.

.(2)ClassBandCsourcesshallbestabilized withinanapprovedsolidification orencapsulation media.Activated Carbona0b.Activated Carbonfromvendorprovidedliquidwastedemineralization istransferred directlytoaliner/High Integrity Container.

Thiswastestreamisconsidered Activated-Carbon.Theconstituents ofthiswastestreammayincludevarioustypesofcharcoal, ionspecificcarbonfiltermediaandcorrosion andcontaminants fromliquidwastestreams.

4tV NDAP-gA-0646 Revision4Page27of63C.Activated Carbonmaybesolidified, dewatered orprocessed byvolumereduction methodswhichincludedrying,incineration, compaction, useasfill-materials orotherevaluated methods,onacasebycasebasis.6.2.116.2.126.2.13AWasteTypethatiscombinedwithaknownamount.ofhazardous wasteor"HixedWaste"shallbeprocessed forfinaldisposalpendingapprovalobtainedfromtheprocessing anddisposalfacilities, Environmental Protection Agency,U.S.NuclearRegulatory Commission andotherregulatory agenciesasrequired.

Wastetypescontaining chelating agentswithintherangeofO.lto8.0percentbyweightshallbeprocessed toastablewasteforminaccordance withandauthorized bydisposalfacilityrequirements andapprovals.Variousothermaterials notspecifically identified aswastetypeswillbeevaluated forsolidification, dewatering volumereduction orotherprocessing onacasebycasebasis.6.3RADIOACTIVE WASTEANALYSISANDCLASSIFICATION 6.3.16.3.2Radionuclide concentrations ofradioactive wasteareusedtoclassifywasteforshippinganddisposal.

Radionuclide concentrations shouldbedetermined baseduponisotopicanalysis, volumeandweightoffinalwasteform.The10CFR61Compliance Programestabl.ishes amethodology forcharacterizing radioactive wastethroughtheuseofcorrelation factors.Thisprogramshallrequireasaminimumthat:a.Samplesrepresentative ofSusquehanna's wastestreamsarecollected andanalyzedsuchthatresultsareobtainedfromadesignated laboratory atleasteverytwoyears(ClassA)fordevelopment ofspecificcorrelation factors.Wastestreamsknownorsuspected tobeclassified Class8orClassCshouldbeanalyzedonanannualbasis.

1'I NDAP-OA-0646 Revision4Page28of63Technical basisdocumentation andjustification ofcorrelation factorsaredeveloped foreachwastestreamand'areacceptable foruse.Periodicevaluations andnecessary adjustments toestablished ratiosareperformed inatimelymanner.C.Co'rrelation factorsarere-evaluated following significant changes(greaterthanafactorof'0)inplantoperations (suchassignificant changesinfuelleakage,radwasteoperations, orequipment).

Determination ofwasteclassification shallbeinaccordance with10CFR61.55, WasteClassification, anditssupplementary BranchTechnical PositiononRadioactive WasteClassification asfollows:*.b.C.ClassA-Usuallysegregated fromotherwasteclassesatthedisposalfacility.

Physicalformandcharacteristics shallmeettheminimumrequirements specified in10CFR61.56(a):

If.thestability requirements in10CFR61.56(b) aremet,thewastedoes.nothavetobesegregated fordisposal.

ClassB-Physicalformandcharacteristics

.shallmeetboththeminimumandstability requirements specified in10CFR61.56.

ClassC-Physicalformandcharacteristics shallmeetboththeminimumandstability

~requirements specified in10CFR61.56.

Inaddition, measuresshallbetakenatthedisposalfacilitytoprotectagainstinadvertent intrusion.

Isotopicanalysismaybeperformed by:Gammaspectrometry ofasampleanduseofcorrelation factors.b.Directgammaspectrometry ofwasteanduseofcorrelation factors.C.d.Completeradionuclide analysisofwastesample.DosetoCuriecalculations.

0 NDAP-gA-0646 Revision4Page29of63e.Activation analysis.

Volumeandweightoffinalwastemaybedetermined by:ta.Calculation usinganalytically derivedsampledensities..

b.Calculation usingstandardwastedensities.

c.Directmeasurement ofvolumeandweight.d.Acceptable methodsdescribed intheTechnical PositiononConcentration Averaging

'andEncapsulation.

Ifsamples.ofwasteareusedforclassification, samplingprogramshallinclude:a.Samplesshallbeobtainedandanalyzedforeachbatchof.wetwasteifpractical andALARA.b.Preferentially, samplesshouldbetakenforanalysisfollowing processing intoafinal'aste form.c.Samplestakenpriortofinalprocessing shouldenableresultsofsampleanalysistobedirectlytranslated tofinalwasteform.d.HeadresinandActivated Carbonusedforchemicaldemineralization shallbesampledafterhaving'has beendepletedinprocess.e.Solidification/Dewatering ServicesVendororanotherqualified individual shallobtainrequired.

samples.Preparation ofwasteforsamplingoranalysisa~b.WetWasteCollection tanksshallberecirculat'ed inaccordance withapprovedoperating procedures'rior tosamplingoranalysis.

Wasteprocessing insolidification liners/High Integrity Containers shallbemixedinaccordance withapprovedprocedures priortosamplingoranalysis.

6.3.8'.3.9-NDAP-gA-0646 Revision4Page30of63c.Wetwastetobeprocessed mayalsobemixed,recirculated andsampledoranalyzedfrommobileprocessing equipment.

Finalwasteformcontaining amixtureofwastetypesorstreamsshallbeindividually.

analyzedtodetermine radionuclide concentrations.

Thesummation ofeachindividual radionuclide concentration shallbeusedtocharacterize thefinalwasteformforshippingand:disposal.

Wastetypesorstreamsofdifferent wasteclasses(estimated byhistorical precedent orprojected analysis) shallnotbemixed.EDeviations fromsamplingandanalysisrequirements shallbeapprovedbyChemistry Supervisor andEffluents Management Supervision.

Solidified wasteshallbetestedand/ortreatedtoensureitisnotcapableofgenerating quantities of'lammable ortoxicgases,vaporsorfumeswhich'aybeharmfultopersonstransporting,

handling, storingordisposing ofthewaste.6.4.16.5RADIOACTIVE WASTESOLIDIFICATION

()6.4TESTING/TREATMENT

'OFSOLIDIFIED RADWASTEFORCOMBUSTIBLE'GASES

(')6.5.1GeneralRequirements a0b.C.d.WetWasteTypeswhichmaybesolidified inHighIntegrity Containers areEvaporator Concentrates.,

MixedSolids,Condensate/Radwaste.

Demineralizer BeadResin,RWCUFilterMediaandLiquidOilWasteorPetroleum BasedMaterial, Cartridge Filters,SolidSealedSourcesandActivated Carbon.HighIntegrity Contasners shallbeusedtomeetthestability crite.'.inaccordance withfederalanddisposalfacilityregulations.

Solidification processing shallbeconducted byqualified SSESorSolidification/Dewatering/

ServicesVendorpersonnel.

Thesolidification processshallbeoperatedinaccordance withapprovedprocedures.

Procedures shallspec'ifywastestream,amountsofsolidification agentandadditives ormethodfordetermination.

NDAP-gA-0646 Revision4Page31of63WastePreconditioning a.Wastepreconditioning requirements shallbedetermined bychemistry analysis.

b.C.Preconditioning ofwasteshallbeperformed ifrequiredpriortodetermining mixingratios.Wastepreconditioning isrequiredwhenanyofthefollowing conditions exist:(1)AhighorlowpHcondition, asdetermined bychemicalanalysis; (2)Liquidcontentofthebatchisoutoftheacceptable envelopeforsolidification.

.(3)Solidscontentofthebatchisoutoftheacceptable envelopeforsolidification.

(4)Knownpotential problemchemicals andconstituents withinwastethatmayadversely affectsettingandstability ofcement-solidified wasteform.d.e.Wastepreconditioning shallbeperformed inaccordance withapprovedprocedures toensurewasteiswithintheacceptable envelopeforsolidification.

Uponcompletion ofwastepreconditioning, additional samples,asrequired, shallbeobtainedinaccordance withRadioactive WasteAnalysisandClassification sectionofthisprocedure.

Determination ofHixingRatiosa~b.cDetermination ofmixingratios.shallbeperformed foreachwastebatchtobeprocessed.

Deviation fromtherecommended mixingratiosshallbereviewedbyPlantOperations ReviewCommittee (PORC).Chemistry Groupdetermines:

(1)Densityofthewastesamples.

NDAP-gA-0646 Revision4Page32of63d.e.(2)SpecificgravityofSodiumSulfateSolutioninEvaporator Concentrates.

Solidification/Oewatering/Services Vendordetermines ifthefinalmixingratiosarewithintheacceptable envelopeforsolidification.

Forsolidification performed onsite:(1)Chemistry Groupshallperformtestsolidification ofwasteasrequiredbyTestSolidification sectionofthisprocedure.

(2).Chemistry Groupdetermines mixingratiostoensurepropersolidification.

Forsolidification performed offsite:(1)Solidification/Dewatering/Services Vendor,shallperformtestsolidification ofwasteasrequiredbyTestSolidification sectionofthisprocedure.

(2)Solidification/Oewatering/Services Vendordetermines mixingratiostoensurepropersolidification.

TestSolidification

'a~Testsolidification shallbeperformed tosupport.wastemixingratiosasfollows:'(1)Atleasteverytenth(10th)batchofthesamewastestream.(2)Whensampleanalysisfalloutsidetheestablished rangeandcriteriaindicating achangeinwastecharacteristics.

(3)Whenitisbeli'eved thatsomeunexpected orabnormalcontaminant maybepresent.(4)Whenrequested byRadwasteSupervisor.

NDAP-gA-0646 Revision4Page33of63(5)Hixingofmaterials shallbeaccomplished inamannerthatduplicates, totheextentpractical, mixingconditions thatareobtainedwithfull-scale mixingincontainer.

(6)Curingshallbeperformed underconditions similartothoseusedinlaboratory qualification testprogram.Uponfailureofatestsolidification, anLCOisentered,'dditional samplesshallbeobtained, alternative solidification parameters aredetermined andasubsequent testverifiessolidification.

Testsolidification shallbeperformed oneachsubsequent batchofthesamewastestreamuntilatleastthree(3)consecutive initialtestsolidification

'emonstrate acceptability inaccordance withTechnical Specification 3/4.11.3.

gualityControlshallverifytestsolidification acceptability andindicatetheacceptability onthesurveillance documentation.

Theacceptability requirements aredefinedinthePCPSurveillance Specimensectionofthisprocedure.

Extrasamplevolumeforbackuptestingshallbedisposedofafteracceptable container checksarecompleted.

.HighIntegrity Container testsolidification billetsshouldbedisposedafteracceptable container checksarecompleted.

Testsolidification shouldbeperformed withsamplesfromwasteobtainedasfollows:(1)Inaccordance withRadioactive MasteAnalysisandClassification sectionofthisprocedure.

(2)Samplingofthesolidsinthecontainer andtheliquidsusedfor.hydration, thenmixedtotheratiosthatexistinthecontainer.

A'II' NDAP-gA-0646 Revision4Page34of63f.g.TestSolidification Procedures shallbedeveloped foreachspecificwastetypeasrequired.

h.Cement,water'ype andadditives tobeusedinactualsolidification.

shallbeusedin,preparation oftestsolidification.

PCPSurveillance Specimens a.HighIntegrity Container testsolidification billetsshallbeexaminedandtestedforacceptability afterthespecified curetime'for:(1)Liquidonsurfaceofsolidified productlessthat1.0Xbywastevolume.(2)Visibledefects,suchascracking,

spalling, ordisintegration.

(3).Strengthbyphysically pokingthesurfaceofsolidified productwitharigid'nyielding device.Nominalsurfacedentingisacceptable.

b.Ifcementsol'idification insteellinersisNRCapprovedtoprovidestability, PCPsurveillance specimenexamination testingandreporting isrequiredinaccordance withtheBranchTechnical PositiononWasteForm,Rev.I.CuringTime.a.Aminimumof30hoursshallbeallowedforcuringpriortocappingortransporting container.

b.Thecontainer maybemovedduringthefirst"hour aftersolidification butmustremainundisturbed fortheremaining 29hours.c.,Deviations fromminimumrequiredcuringtimeshallbeapprovedbyRadwasteSupervisor andjustifications documented inremarkssectionofSolidification Record.

NOAP-gA-0646 Revision4Page35of63Solidification Productgualitya~Solidification productqualityisassuredbyuseofpredetermined mixingratiosofwaste,cementandadditive.

Liquidtobeusedforsolidification shouldbedemineralized water.b.'re-qualification mixingratiosarebasedonlaboratory testingusingnon-radioactive wastematerials.

c.Hixingratiosarere-enforced bythefollowing:

(I)Testsolidification performed periodically asstatedinTestSolidification sectionofthisprocedure.

(2)Visuallyandphysically checkingatleasteveryfifth(5th)container ofthesamewastetype.d.Container checksshallconsistof:(I)Avisualcheckofsolidified productforliquidonsurfaceofproductnottoexceed.1.0Xbywastevolume.(2)Physically pokingthesurfaceofsolidified productwitharigidunyielding devicepriortocapping(Nominalsurfacedentingmayoccurandisacceptable).

e.gualityControlshallverifyacceptability ofsolidified productwhencontainers arechecked.I'.Oeviation fromthecontainer checkingrequirement, shallbeapprovedbytheRadwasteSupervisor.

HandlingofUnacceptable Solidified WasteContainers.

a.b.Ifasolidified wastecontainer doesnotmeetacceptability requirements, aCondition Report(CR)shallbeissued.Ifthereasonforunacceptability isfreeliquid:(I}Thefreeliquidwi11beremoved;or NDAP-gA-0646 Revision4Page36of63(2)Extracement/additive willbeaddedtosolidifyfreeliquid.Ifportionsoralloftheproductdidnotsolidifyafterthreedays:'(I)Thewastecontainer willbecappedandplacedinastoragelocationandperiodically checkeduntilsuchatime:productisacceptable; or(2)Additional solidification agentsmaybeaddedtoachievesatisfactory solidification, asdetermined bytheRadwasteSupervisor.

Iftheproductsolidifies prematurely priortocompleting theadditionofrequiredamountofcement-andadditive, ascalculated onthesolidification calculation sheetforthespecificprocedure used,thefollowing isrequired:

(I)Atestsolidification shallbeperformed usingtheactualratioofcementandwasteinthecontainer, providedsufficient

'samplevolumeremainstocompletethisitem.(2)gualityControlshallchecktheproductforacceptability inaccordance withContainer Checkssectionofthisprocedure.

(3)"Thecontainer isconsidered tomeetacceptable wasteformcriteriaforshippingprovidedthesubsequent testsolidification and/orcontainer checksareacceptable to-;alityControlandconcurrence ofthe'Radwaste Supervisor isobtained.

(4)TheaboveapplyonlyiftheEffluents Management Supervisor determines thattheproductcanbeclassified as"ClassAUnstable" orisplacedinaHighIntegrity Container orstructure thatprovidesstability inaccordance withIOCFR61andthedisposalfacilitycriteria.

tr NDAP-gA-0646 Revision4Page37of63e.Iftheproductdoesnotsolidifyproperlyinaccordance withthespecificsolidification procedure, thefollowing isrequired:

(I)Anevaluation ofthelinershallbemadebythefollowing personnel:

(a)Effluents Management Supervision (b)Solidification Vendor-Operations (c)Solidification Vendor-Engineering (2)Disposalfacilities

.shallbecontacted andrequirements forreceiptofthelinerinquestionshallbedefined.(3)Alternative packaging/processing shallbeevaluated.

(4)(5)Recommendations forfinaldisposition shallbemadetothePowerProduction Engineer-Effluents Management.

Finaldisposition shallbereviewedbyPlantOperations ReviewCommittee (PORC).(6)Recordsshallbekeptanddocumentation supportive offinaldisposition attachedtothesolidification recordpackage.(7)Thelinermaybeshippedafterg.C.reviewofdocumentation iscompleteanddisposalfacilityconcurrence isreceivedinletterform.f.Specificinstructions shallbeestablished forhandlingunacceptable solidified wastecontainer onacasebycasebasis.g.equalityControlshallre-verify acceptability ofsolidified productbyperformance ofContainer Checks.CappingofSolidified WasteContainers a.Therequirements ofSolidification Productequalitysectionofthisprocedure shallbemetpriortocappingthecontainer.

4llII4*1a NDAP-QA-0646 Revision4Page38of63b.Ifthecontainer isnotequippedwithapassiveventanditscontentsarewithintherequirements ofLowSpecificActivity(LSA)ensureoneofthefollowing:

(1)lhecontainer shouldbesnippedwith>n(10)tendaysaftercapping;or(2)Ifacontainer hasbeencappedforlongerthan(10)days,itshallbeopened,vented,andre-capped within(10)tendaysofshipment.

c.Iftheconta'incr exceedsthelimitsforLowSpecificActivityandcontainswaterand/ororganicsubstances whichcouldradiolytically generatecombustible gases,determination mustbemadesuchthatthefollowing criteriaaremetoveraperiodoftimethatistwicetheexpectedshipment.

time:(1)Thehydrogengenerated shallbel.imitedtoamolarquantitythatwouldbenomorethan5Xbyvolumeofthecontainer gasvoid'1(2)Thecontainer andshippingcaskcavityshallbeinertedwithadiluenttoassurethatoxygenislimitedtoless.than5Xbyvolumeinthoseportionsofthepackagewhichcouldhavehydrogengreaterthan5X;Solidification AgentControla.PortlandCement-ASTIC-150TypeIshallbeusedforthemobilesolidification process.b.Othersolidification agentsmaybeusedonlyafteracceptable testingoftheagenthasbeencompleted thatdemonstrates acceptable solidification anddisposalfacilityapprovalhasbeenobtained.

ItI NDAP-gA-0646 Revision4Page39of63C.Documented Certification isnotrequiredformaterials receivedinbagsprovidedmaterialverification canbeobtainedasfollows:(1)Cementisacceptable providedthebagconta>ning tnecementindicates thatcementisPortlandTypeI.(2)SodiumSilicateisacceptable provided'thebagcontaining theadditiveindicates Anhydrous SodiumNetasilicate.

(3)Otheradditives areacceptable providedthecontainer isclearlymarkedindicating thetypeofadditive.

deOtheradditives maybeusedforenhancement ofsolidification processasspecified inthesolidification procedure anddocumented in'hesolidification records.Radioactive WasteSolidification RecordsASolidification RecordSheet(FormNDAP-gA-0646-1) shallbecompleted foreachcontainer filledwithsolidification products.

Completion oftheSolidification RecordSheetandthe.requiredaccompanying documentation shallbeas.follows:a.TheRadwasteSupervisor isresponsible forinitiating thisformandcompleting Parts1and2.b.Effluents Management Supervision,

.Chemistry andSolidification/Dewatering/Services Vendorpersonnel shallprovideandcheckofftherequireddocumentation specified inPart3.equalityControlshallprovidereviewasrequiredfortheSolidification Records.

NDAP-gA-0646 Revision4Page40of636.6RADIOACTIVE WASTEDEWATERING 6.6.1GeneralRequirements a~b.c~d.e.WasteStreamswhichmaybedewatered ineither.HighIntegrity Containers orsteellinersare,LRWFilterMedia,Ultrasonic ResinCleanerWaste,SumpSludge,RWCUFilterMedia,Condensate/Radwaste Demineralizer BeadResin,.Cartridge FiltersandActivated Carbon.Thetypeofcontainer usedshallbebasedonthewasteclassification andstability criteriainaccordance withfederalanddisposalfacilityregulations.

Dewatering ofRadioactive Wasteshallbeperformed byqualified SSESorSolidification/

Dewatering ServicesVendorpersonnel.

Dewatering ofRadioactive Wasteshallbe:performed inaccordance withapprovedprocedures.

Dewatering procedures shallbebasedondocumented testdatathathasdemonstrated theabilitytoachievefreeliquidlimitsasspecified bydisposalfacilities andapplicable regulatory agencies.

Liquidvolumeanddrainagecalculations andactualdrainageverification mayalsobeusedtomeetfreeliquidlimits.HighIntegrity Containers shallbeusedfordisposalwhentheconcentration ofradionuclides withhalf-lives greaterthan5yearsexceeds1pCi/cc.Eachwastestreamwhichmaybedewatered shouldbecharacterized bytheSolidification/

Dewatering ServicesVendortoensurethe,operating parameters andeffectiveness ofthedewatering systemareinaccordance withtheparameters established intheTopicalReport.

0 NDAP-gA-0646 Revision4Page41of63Dewatered ProductControla.Thefinaldewatered productshallcontainlessthanIXnon-corrosive freeliquidforHighInteoritv Containers and0.5Xforsteelljners.equalityControlchecksshallbeperformed onprocesssteps.b.Ifadewatered wastecontainer does'otmeet:acceptability requirements, aCondition Report(CR)shallbeissued.c.Specificinstructions shallbeestablished forhandlingunacceptable dewatered wastecontainer onacase-by-case basis.d.Deviation fromthecontainer checkingrequirement shallbeapprovedbythePowerProduction Engineer-Effluents Hanagement.

Radioactive WasteDewatering RecordsADewatering RecordSheet(FormNDAP-gA-0646-2) shallbecompleted foreachcontainer filledwithdewatered wastestreams.Partsoftheformshallbecompleted bythefollowing responsible individuals orgroups:a.TheRadwasteSupervisor isresponsible forinitiating thisformandcompleting PartsIand2.b.Chemistry GroupshallcompletePart3SamplingandAnalysis.

c.Effluents Management Supervision, Chemistry andSolidification/Dewatering/Services Vendorpersonnel shallprovideandcheckofftherequireddocumentation specified inPart4..d.gualityControlshallprovidereviewasrequiredfortheDewatering Records.

NDAP-gA-0646 Revision4Page42of636.7HIGHINTEGRITY CONTAINERS (HIC)6.7.1StorageofHighIntegrity Containers a~Vectra,RadlokandCNSIHighIntegrity containers

~niC)storedlnu)rectsullii/Ill.vllnareaswherethereisastrongsourceofultraviolet radiation shallbefilledanddisposedofwithinoneyearofmanufacturing

date.6.7.2b.C.Usesa0OncefilledaHighIntegrity Container.may bestoredforaperioduntilatotalof.one(1)yearofultraviolet radiation isreceived.

Shortexposures (i.e.,severalhours)tosunlight, suchasoccurring duringshipmentandonsitetransferneednotbecountedwhendetermining totalultraviolet exposure.

tofHighIntegrity Containers HighIntegrity Containers maybeusedtopackagethefollowing wastematerials fordisposal:

(1)Dewatered beadresin,powderedresinand'diatomaceous earth.(2)Compressible andnon-compressible solidwastes.(3)Filterelementsandcartridges.

(4)Solidified resins,sludges,andliquidwastes.(5)Incinerator ash,residuals, orequivalent waste.whichhasbeenrenderednon-dispensable i-'indingmatrix..(6)Otherdewatered anddrymaterialprovidedconcurrence isreceivedbycontainer vendoranddisposalfacility.

NDAP-gA-0646 Revision4Page43of63PriortousingaHighIntegrity Container foraspecificwastematerial, procedures shallbeestablished todefinethespecificrequirement thatshallbemetduringuseofthecontainer.

Theprocedures shallcontain:Documentation requirements thatspecificconditions havebeenmetsuchasinspection andexposuretodegrading conditions.

Instructions astohowtohandleandproperlyclosethecontainer.

Instructions foron-sitestorageofloadedcontainers forultimateshipmentfordisposal.

Theprocedures shallprovideamethodfordocumenting requiredinformation relevanttothecontainer frominitialreceipttoshippingfordisposal.

Requiredinformation shallbebaseduponthecontainer certificate ofcompliance anddisposalfacilityrequirements.

Retention andutilization ofthedocumentation shallbedefinedintheprocedures.

Theprocedures shallestablish specificgualityControlinspection requirements.

PriortothefirstshipmentofaspecifictypeofHighIntegrity Container, authorization shallberequested fromtheapplicable regulatory.

agencygoverning useofthecontainer inquestionatthedisposalfacilityofconcer'n.

NDAP-(}A-0646 Revision4Page44of63HighIntegrity Container Limitations HighIntegrity Containers areapprovedforuseprovidedthefollowing physicallimitations ofthewastearemet:(1)VectraPayloaddensity(2)Loadingtemperature

<147'ms/cc<170'F(3)VectraEL-50N.S..loadedweight:<4200lb(4)VectraEL-142N.S.loadedweight:g8250lb(5)VectraEL-142S.loadedweight:611250lb(6)VectraEL-190N.S.loadedweight:<11950lb(7)VectraEL-190S..loaded weight:<14800lb(8).VectraEL-210N.S.loadedweight:.<13000lb(9)VectraEL-210Sloadedweight:<17300lb(10)CNSISmallloadedweight<2500lb(11)CNSIHediumloadedweight<2500.lb(12)CNSILargeloadedweight<2500lb(13)Radlok179loadedweight<18500lb(14)Radlok195loadedweight(15)Enduropak 105loadedweight(16)Enduropak 205loadedweight(17)Enduropak 150loadedweight<18500lb<1700lb,<1900lb52400lbb.Themaximumconcentration ofradionuclides withhalflivesgreaterthan(5)fi.veyearsthatmaybedisposedofinaHighIntegrity Container is350pCi/cc.Otherwasteformsshallnotexceed1.0X10radsmaximumintegrated dosetothecontainer.

NDAP-gA-0646 Revision4Page45of63c.Thepolyethylene HighIntegrity Containers shall.notcomeintocontactwithmaterials listedinAttachment E.d.Apassiveventdesignshallbeincorporated intothecontainer torelieveinternalcontainer-pressure.

Closureof,HighIntegrity Containers ClosureofHighIntegrity Containers shallbecompleted inaccordance withapprovedprocedures.

b.C.d.Ifthecontainer isnotequippedwithapassiveventanditscontentsarewithinthelimitsofLowSpecificActivityensureoneofthefollowing:

(1)Thecontainer isshippedwithin(10)tendaysafterclosing;or(2)Ifthecontainer hasbeenclosedforlongerthan(10)tendays,itshallbeopened,vented,andre-closed withinten(10)daysofshipment.

Ifthecontainer exceedsthelimitsforLowSpecificActivityorcontainswaterand/or'rganicsubstances whichcouldradiolytically generatecombustible gases,determination mustbema'desuchthatthefollowing criteriaaremetoveraperiodoftimethatistwicetheexpectedshipmenttime:(1)Thehydrogengenerated shallbelimitedtoamolarquantitythatwouldbenomorethan5Xbyvolumeofthecontainer gasvoid;ol(2)Thecontainer andshippingcaskcavityshallbeinertedwithadiluenttoassurethatoxygenislimitedto<5Xbyvolumeinthoseportionsofthepackagewhichcouldhavehydrogengreaterthan5X.Step6.7.4.band6.7.4.cshallalsoapplytodewatered wasteinsteelliners.

NDAP-gA-0646 Revision4Page46of636.8IRRADIATED HARDMAREPROCESSING ANDDEMATERING 6.8.1GeneralRequirements a.Processing

'anddewatering ofIrradiated

'Hardware

~shallbe.performed by.qualified SSESorvendor='ersonnel.

b.Processing anddewatering ofIrradiated Hardwareshallbeperformed inaccordance withapprovedprocedures..

C.d.agencies.6.8.2.Dewatered Product'.

ControlIrradiated Hardwareconsisting ofnon-fuelSpecialNuclearHaterialshallbeinventoried duringprocessing inaccordance withNDAP-(A-0337.

Dewatering procedures shallbebasedonliquidvolumeanddrainagecalculations andactualdrainageverificatiom todemonstrate the.ability.

toachievefreeliquidlimitsasspecified bydisposalfacilities and'applicable reg'ulatory 6.8.3a.The'finaldewatered productsha11containlessthan0.5Xfreeliquidforsteelliners.b.gualityControlchecksshallbeperformed onprocesssteps.Irradiated HardwareProcessing andDewatering Recordsa.Allrecordsgenerated shallbecompleted andfiledinaccordance withapprovedimplementing procedures.

6.9CONTAINER INSPECTIONS 6.9..1gualityControlshallinspectcontainers tobeusedforsolidification, dewatering, andotherpackaging fordisposal.

6.9.2'hisinspection shallassurethatpriortouse,thecontainers tobeusedforsolidification, dewatering, orotherpackaging areintactandtheirinternals arefreeofanyvisualdamagethatwouldpreventthemfromperforming theirintendedfunction.

NOAP-QA-0646 Revision4Page47of636.9:3.Packagesshallmeetthegeneralcriteriafornormaltransport conditions inaccordance withtherequirements of49'CFR.TypeApackagesshallmeettheadditional designrequirements specified in49CFR.6.10WASTECONTAINER SPACEUTILIZATION 6.10.1Wastevolumeshallbemaximized within.theguidelines ofspecificprocedures tominimize.

'.potential voidspaceatthetopofwastecontainer.

aftersolid)ication ordewatering,'is complete.

Pa.Additional radioactive materialshouldbe'ddedonlyaftertheinitialwastevolumeisinfinalformandsampledandtheaddedwastevolumeisinfinalformandsampled.b.Theadditional materialmaybedrawnintocontainers abletowithstand higherexternalpressures withoutdegredation bycreatinganareaoflowpressureinsidethecontainer, such-aswithsteelliners.6.10.26.10.36.10.46.11STORAGEOFc.Forallothercontainers, theadditional

~material.'shall beaddedviamechani'cal processes.or'by otherconveyance whichdoesnotexerthigherexternalpressures.

• -':Wastevolumes.shallmeetorexceeddisposalsitecriteria, Ifwastevolumeislessthan"disposal

'acilitycriteria; requirement's fordisposalofthecohtainer inquestionshallbedefinedbythedisposalfacility.

Spec'ific wastevolumescommitted tobythe,Solidification/Dewatering/Services Vendorshallbemetorotherwise justified astowhywastevolumeswerenotachieved.

Susquehanna Guaranteed Solidified/Dewatered WasteVolumeRecord,FormNDAP-gA-0646-3, shall'ecompleted bytheSolidification/Dewatering/

Servicesvendorpersonnel, approvedbyRadwasteSupervisor andshallbeusedtotrack.solidified/dewatered wastevolumesachievedineachindividual container.

PACKAGEDRADIOACTIVE WASTE6.11.16.11.2RadwasteSupervisor shallprovideSolidification and/orDewatering RecordsheetsthathavebeenreviewedbygualityControlpersonnel statingthatprocessed wastehasbeensolidified orde-watered inaccordance withtheProcessControlProgramandmeets~theapplicable shippinganddisposalcriteria.

Solidification andDewatering Recordsshallincludetheisotopicmix,'isotopic concentration ofthewastethatwaspackaged, thetotalvolumeofthewaste,andtheamountofwater,cementorothersolidification agentused,asappropriate.

NDAP-gA-0646 Revision4Page48of636.11.36.11.46.11.56.11.6Solidification andDewaterino Recordsshallbepartofthepermanent shippingrecordsandadheretorequirements oftheProcessControlProgram.Formaterials packagedinahighintegrity container, documentation shallbemaintained onHICstorageandpre-shipment checklist info'rmation.

Packagedradioactive wasteshallbestoredinareas".designated byHPForemanEffluents Management.

Storageofpackagedradioactive wasteintheLowLevelRadwasteHolding'acility (LLRWHF)shal,lbeinaccordance withapprovedprocedures.

Aninventory ofstored,packagedwasteshall.bemaintained inaccordance withapprovedprocedures.

6.12TRANSPORTATION, SHIPPINGANDDISPOSALREGULATIONS 6.12.1Specificregulatory documents shallbemaintained onsiteinastatusthatiscurrent.Specificregulations thatshallbemaintained includebutarenotlimitedtothefollowing:

a~10CFR71Packaging ofRadioactive Materialfortransport'nd transportation ofradioactive materialundercertainconditions.

b.C.d.e.49CFR100-199Transportation.

Chem-Nuclear SystemsInc.BarnwellS.C.disposalsiteoperating licensenumber097StateofSouthCarolina, asrequired.

Chem-Nuclear SystemInc.NRCMaterial.

License12-13536-01, asrequired.

Chem-Nuclear SystemInc.BarnwellS.C.disposalsiteoperating proc>".resandsitecriteria, asrequired.

Scientific EcologyGroupLicensesR-73008-E94, R-01052-A91.

g.CaskManualsforcasksofwhichPP&Lisanauthorized user.h.AcopyofthelicenseforeachfacilitytowhichRadioactive Materialissent.

'(

NDAP-gA-0646 Revision4Page49of63i.10CFR61Licensing requirements forlanddisposalofRadioactive Waste.6.12.2Procedures applicable totransportation, shippinganddisposalshall'bedeveloped.

'a~Procedures shallbeestablished andmaintained toprovidedirections andassureregulatory compliance formanifesting, whichincludeapplicable federal,state,anddisposalfacilityregulations, andNRCguidance.

b.Procedures shallcontaincheckofflistswhereandwhenapplicable toassurespecificattention ispaidtothecriticalfunctionbeingcontrolled.

6.12.3-c.Procedures shallcontaingualityControlnotifications orholdpoints.Computersoftwareusedtoimplement applicable portionsoftheProcessControlProgramshallbeinaccordance withNDAP-(A-0801.

6.13SHIPPINGOFRADIOACTIVE WASTE6.13.16.13.26.13.36.13.4Allradioactive'aste shallbeshippedbyEffluents Management.

Allradioactive wasteshippedfromSSESshallonlybetofacilities licensedtoreceivethewasteandinaccordance with10CFR20,10CFR71and49CFR100-199.

DryActiveWaste(DAW)"shouldnormallybeshippedasTypeAquantities andtherefore donotrequirespecificlicensedcontainers.

Wastecontainers shallbeplacedinaUSNRCapprovedlicensedshippingcontainer ifit:'a~b.C.ExceedsTypeAquantities Exceeds1000mr/hroncontactExceeds1000dpm/100cmloosesurfacecontamination ontheexteriorofthecontainer.

NDAP-gA-0646 Revision4Page50of63Thespecificconditions oftheCertificate ofCompliance foreachapprovedshippingcaskshallbestrictlyadheredto.Packagedwaste;may beshippedunshielded if:a.Contactdoseratesarelessthan200mrem/hranddoseratesat6feetarelessthan10mrem/hr.

b.CuriecontentofthepackageshallbeaTypeAquantity.

c.Container shallbeaminimumofastrongtightcontainer.

Priortotheshipmentofapackageofradioactive waste,theHPForemanEffluents Nanagement shallassurethecontainer issurveyedforcontactdoseratesandsurfacecontamination.

Decontamination, ifrequired, shallbedoneunderthedirection oftheHPForemanEffluents Management.

Decontamination maybewaivedbaseduponradiological conditions.

Allvehiclesusedtotransport radioactive wasterequiring thevehicletobeplacarded shallbecheckedforadequateoperation andsafetyconditions.

AllRadwasteshipments fromSSESshallnormallybevia"Exclusive Use"vehicles.

Specificinstructions giventothedriverinclude:a.Expectedrouteoftraveltohisfinaldestination.

b.Maintaining "Exclusive Use"status.c.Specificactionstobetakenintheevent.ofanaccident.

Novehiclecarryingradioactive wastethatisoverweight shallleaveSSESwithoutaPennsylvania overweight permit.a.ADAMshipmentorothershipmentcapableofhavingitsweightadjusted, shallnotbeallowedtoleaveSSESoverloaded.

Anoverloaded condition foranyvehicleisbasedontotalweightandweightperaxle.

NOAH'-QA-0646 Revision4Page51of636.13.11IntheeventaccessisdeniedtoSSESatalloperating disposalfacilities, PP8LwillprovidecarrierwithaletterstatingthatSSESwillmeetallapplicable federal,state,andcompactrequirements forreceiptbackoftheradioactive waste/material incarrier's possession.

6.14SHIPMENTCONFIRMATION Ifdisposalsiteshipmentacknowledgement isnotreceivedwithin18daysfromdeparture fromSSES,Effluents Management Supervision shallconductatraceinvestigation forshipmentlocation.

Ifthedisposalfacilityshipmentreceiptcannotbeconfirmed within20days,aCondition Report(CR)shallbegenerated.

6.15CHANGESTOTHESOLIDRADIOACTIVE WASTEPROCESSCONTROLPROGRAM6.15.1AnychangesasdescribedintheTechnical Specifications, totheSolidRadioactive WasteProcessControlProgramshallbeprovidedintheAnnualRadioactive EffluentReleaseReportfiledwiththeNRC.6.15.2AnychangestotheSolidRadioactive WasteProcessControlProgramshallbeapprovedbyPlantOperations ReviewCommittee (PORC)priortoimplementation.

()6.16EVALUATION OFPROCESSOROPERATIONAL CHANGES6.16.16.16.2Changesinradioactive wasteprocessing oeoperational changesshallbeevaluated todetermine anyimpactsonwastecharacteristics and/orform.Evaluation shouldincludeasaminimum:a.Operational evaluation ofprocessing impacts:b.C.Chemistry evaluation ofchangestosamplingandanalysismethodology.

Effluents Management evaluation ofpackaging and/orshippingimpacts.d."Effluents Management evaluation forlOCFR61compliance.

NDAP-gA-0646 Revision4Page52of63e.Solidification/Dewatering ServicesVendorwastestreamcharacteristic evaluation ofthedewatering/solidification systemoperating parameters andeffectiveness.

()6.17REPORTING OFMISHAPSINVOLVING LOWLEVELWASTEFORMS6.17.1IOCFR61establishes theminimumandstability requirements forLowLevelWaste(LLW)forms.10CFR20requirescertification thattheprocessed wastesatisfies therequirements of10CFR61.Mishapswhichmayimpactthefinalwasteformshallbereportedto'theNRC.6.17.2Typesofmishapswhichshouldbereportedinclude:a.b.C.Failureofhigh-integrity containers usedtoensureastablewasteform.Container

'failurecan'eevidenced bychangedcontainer dimensions,

cracking, ordamageresulting frommishandling (e.g.,droppingorimpacting againstanotherobject).Misuseofhigh-integri tycontainers, evidencedbyaquantityoffreeliquidgreaterthan1percentofcontainer volume,orbyanexcessive

(>l5X)voidspacewithinthecontainer.

Production ofacementsolidified ClassBorCwasteformthathasanyofthefollowing characteristics:

(1)Containsfreeliquidinquantities exceeding 0.5percentofthevolumeofthewaste.(2)Containswastewithradionuclides inconcentrations exceeding thoseconsidered duringwasteformqualification testingacceptedbytheregulatory agency,whichcouldleadtoerrorsinassessment ofwasteclass.(3)Containsasignificantly different wasteloadingthanthatusedinqualification testingacceptedbytheregulatory agency.

.NDAP-gA-0646 Revision4Page53of63(4)Containschemicalingredients notpresentinqualification testingacceptedbytheregulatory agency,andthosequantities aresufficient tounacceptably degradethewasteproduct.(5)Showsinstability evidenced bycrumbling,

cracking, spalling, voids,softening, disintegration, non-homogeneity, ordimensional changes.(6)Evidenceofprocessing phenomena thatexceedthelimitingprocessing conditions identified inapplicable topicalreportsorprocesscontrolplans,e.g.,foaming,temperature

extremes, premature

'orslowhardening, andproduction ofvolatilematerial.

6.17.3d.Failuretoadheretohighintegrity container limitations asrequiredbycontainer certificate ofcompliance.

e.Notification ofviolation bydisposalfacilityregulatory authorities attimeofcontainer receiptfordisposal.

f.Failureofcement-solidified stablewasteformlongtermPCPsurveillance specimens duetoevidenceofsignificant

cracking, spalling, orbulkdisintegration, compression orpenetrometer strengthand.immersion testresults.Requirements forreporting ofmishapsshall.applyonlytoprocessing l.inersandhighintegrity containers containing radioactive wasteinitsfinalproductform.6.17.4ACondition Report(CR)shallbegenerated if.oneofthemishapsmentioned occurs'.18PCPIMPLEMENTING PROCEDURES Procedures requiredforimplementation oftheProcessControlProgramareshowninAttachment D.

NDAP-gA-0646 Revision4Page54of637.0RECORDS7.1TheSolidification RecordsorDewatering Recordsandtheattacheddocuments shallbeforwarded toEffluents Management'Supervision forretention untilsuchtimeasthecontainer identified onRecordisshippedforfinaldisposition.

7.2Whentheidentified container isshippedtheSolidification RecordsorDewatering Recordsandotherdocuments concerning the,Shipmentshallbefiledwiththeshipping'ocumentation andforwarded toDCSforretention.

7.37.4Documentation ofRadioactive WasteShipments shallberetainedasrequiredbySSESTechnical Specifications.

Radioactive wasteshippingdocumentation shallconsistof,butnotlimitedto,thefollowing records:7.4.17.4.27.4.37.4.47.4.57.4.67.4.7Radioactive MaterialShippingManifestEvaluation ofisotopicmixandconcentration Radiological surveysof:a.Vehicleuponarrivalb.Packagetobeshippedc.LoadedvehiclepriortoshipmentVehicleSafetyinspection Check-off sheetforloadingprocedure Documentation ofadherence toProcessControlProgram(i'fapplicable)

Specialinstructions todriver

SOLIDIFICATION RECORDSHEETPARTI:Container Identification Information Attachment ANDAP-gA-0646 Revision4Page55of631.PPELLinerNumber2.Container VendorSerialNumber3.WasteStream(RWCUFilterMediacannotbeentered)4.TestSolidification required?

YESNO(circleone)PART2:Container Selection (RefertoWM-PS-100) 2.3.Estimated LinerContactDoseRates.mR/hrProjected CurieConcentration pCi/gmExpectedWasteClassification/Stability 4.6.Container TypetobeUsedExpectedCaskTypetobeUsed5.EmptyWeightofContainer TbsPART3:I.2.Documentation Checklist FormNDAP-gA-0646-1 (original)

WasteFormDocumentation WM-RP-Forms(original)

SC-068-002 Forms(copy)WasteForm:STABLEUNSTABL'E (circleone)>85%LinerVolumeUtilized:

YESNO(circleone)WasteActivityDocumentation CH-RC-Forms(copy)IsotopicAnalysis(copy)Compostadded/Log entrymadeonCH-TP-055-1 PART4:HealthPhysicsDataLinerRadiological Survey(original)

ActualFilledContainer WeightREMARKS:p.'lllb.(Ifavailable ALARA)WAUOUKASE~EVTEttDATE//FORMNDAP-OA-0646-1, Rev.2,Page1of1(FileR69-I)

DEWATERING RECORDSHEETAttachment 8NDAP-gA-0646 Revision4Page56of63PART1:Container Identification Information 1.PPLLLinerNumber2.Container VendorSerial.Number3.WasteStreamPART2:Container Selection (RefertoWW-PS-100) 2.3.Estimated LinerContactDoseRatesProjected CurieConcentration ExpectedWasteClassification/Stability mR/hrpCi/gm4.6.LinerTypetobeUsedExpectedCaskTypetobeUsed5.EmptyWeightofContainer lbs.awasteSuperv>sor ate>meFORMNDAP-gA-0646-2, Rev.3,(DUPLEX),

Page1of3(FileR69-I)

PART3:SamplingandAnalysisTank/Container sampledDEWATERING RECORDSHEETAttachment BNDAP-gA-0646 Revision4Page57of632.3.SampleNumberWasteStream1sotopicAnalysisattached5..SpecificactivityofDewatered Sample6.a.Dewatered VolumepCi/gmb.Dewatered Weightc.Sampledensitygmgm/ccx62.43lb/ftonCH-TP-055-1 7.Composite added/Log entrymadeTheabovetank/container containing solidshasbeenanalyzedinaccordance withCH-RC-0?5 andfoundtocontaintheisotopesandspecificactivities asindicated ontheattacheddatasheets.emistryuperv>sion atelmeFORMNDAP-gA-0646-2, Rev.3,(DUPLEX)Page'2of3(FileR69-1)

DEWATERING RECORDSHEETPART4:Container ShipmentInformation SummaryAttachment BNDAP-gA-0646 Revision4'age58of633.4.PP8LLinerNumberFormNDAP-gA-0646-2 (original)

WasteFormDocumentation 2..WasteVolumeNN-RP-...,

Forms(original

)Calculated WasteWeightlb/ftx1Talb.ActualFilledContainer Weight100x(Dewatered WasteVolume)lb.(ifavailable ALARA)ft+ftXTvaiTTolume>85%Container VolumeUtilizedYES/NO(Circleone),WasteForm:STABLEUNSTABLEWasteActivityDocumentation JCN-RC-Forms(Copy)IsotopicAnalysis(Copy)(Circleone)PART5:REMARKS:awasteupvateeview()ateoreman.Ngmt.()ateFORMNDAP-(A-0646-2, Rev.3,(DUPLEX),

Page3of3(FileR69-1)

Attachment CNDAP-gA-0646 Revision4Page59of63SUSUEHANNAGUARANTEED SOLIOIFIEO OEWATEREO WASTEVOLUMERECORD2.3.4.5.DateWasteTypeContainer TypeBurialVolumeUseableContainer VolumeLinernumber6.7.Guaranteed HinimumWasteVolumeWasteVolumeAttainedinchesxft>/inchftS8.WasteVolume'ontainer Usage100x(WasteVol.ft>~Guaranteed Hin.WasteVol.ft>)-100DeadbandAssessment VolumeGuaranteed Hin.WasteVol.ft+(0.01XGuaranteed Hin.WasteVol.ftHinimum(-)

fttoMaximum(+)

ft10.Performance Assessment VolumeDeadbandAssessment Vol.ft-WasteVol.ft=ftll..Remarks:

12.Signature Sossscat>onenorepresentative 13.Signature awasteupervisor FORMNOAP-gA-0646-3, Rev.2,Page1of1(FileR69-1)

WASTEPROCESSING PCPIMPLEMENTING PROCEDURE MATRIXAttachment DNDAP-gA-0646 Revision4Page60of63EvaoratorConcentrates

-Solidified PacificNuclearPT-51-WSPacificNuclearOM-114-NS PacificNuclearOH-104MixedSolids-Solidified PacificNuclearPT-51-WSPacificNuclearOM-104PacificNuclearOH-114-NS LRWFilterMediaURCWasteRWCUFilterMed'iaSumSlude-Dewatered

'acificNuclearOH-43-WSWM-RP-107 Condensate RadwasteDemineralizer BeadResin-Solidified PacificNuclearPT-51-WSPacificNuclearON-114PacificNuclearOM-104Condensate RadwasteDemineralizer BeadResin-Dewatered PacificNuclearOM-43-WSWH-RP-106 CartrideFiltersCNSIFO-OP-019 (Overpack)

WH-PS-230 PacificNuclearOH-16-NSWM-RP-105 IISEGSTD-P-22-002 (ResinExpress)'M-RP-104 SEGSTD-P-03-051 WH-RP-108 Page1of3 PCPIMPLEMENTING PROCEDURE MATRIXAttachment DNDAP-gA-0646 Revision4Page61of63Irradiated Hardware-Dewatered'teel LinerNoneDrActiveWasteDAW-PackainWM-PS-210 LiuidOilWaste-Solidified NoneLiuidOilWaste-Decontamination NoneSolidSealedSourcesNoneWASTEANALYSISANDCLASSIFICATION

-10CFR61PacificNuclearOM-45NSWM-RP-008 CH-RC-075 CK-RC-076 CH-TP-OSS WM-PS-155 WM-PS-160 WM-PS-170 TESTINGTREATMENT COMBUSTIBLE GASESWM-RP-009 WM-RP-301 RADIOACTIVE WASTESOLIDIFICATION

-GENERALCEHENTPacificNuclear.OM-114-NS SC-068-002 (TestSolidification)

Page2of3 PCPIMPLEMENTING PROCEDURE MATRIXAttachment DNDAP-gA-0646 Revision4Page62of63RADIOACTIVE WASTEDEWATERING

-GENERALPacificNuclearOH-60-WSWH-RP-010 HIGHINTEGRITY CONTAINERS PacificNuclearOH-16-NSPacificNuclearH-18-NSWH-RP-012 DISPOSALFACILITYREUIREHENTS WM-PS-180 PACKAGING WM-RP-011 WM-PS-401 (LLRWHF)WH-PS-310 WM-PS-311 WH-PS-315 WM-PS-345 WH-PS-351 WH-PS-352 WH-PS-356 (HN-142)(LN-142)(SEG3-82)(CNSI14-'195)(CNSI21-300)(CNSI8-120A)WH-PS-354 (CNSI14-215)WH-PS-316 (SEG14-215)WH-PS-318 (Westinghouse TCT)TRANSPORTATION

-49CFRIOCFR7]WM-PS-100 WH-PS-120 WH-PS-140 WH-PS-180 WH-PS-240 WH-PS-250 Page3of3

~I~Attachment ENDAP-gA-0646 Revision4.Paqe63of63QATERTAPS NOTIOQDATJBLE

'/(TEDo>>vF~i>>~'!~"~.~>>~l~RSAliphatic hydrocarbons (hexane,octane,,bexene,octane,etc.)AcetoneAmylAcetateAmylChlorideAnilineAquaRegia,BenzeneBromineliquidButaneCamphorOilCarbonDisulphide Carbon'Tetrachloride ChlorineliquidChlorobenzene Chloroform Chlorosulfonic acidChromic/sulfuric acidCyclohexanone Dibutylphtalate Dimethylamine Di'eselfuelEthylacetateEthylbutyrateEthylchlorideEthyletherEthylenechlorideEthylenechlorohydrin Ethylenedichloride FluorineFurfuralFurfurylalcoholFuelOilGasolineiodineMethylbromide'ethyl ChlorideHethylethylketone(t1EK)Nethylene ChlorideHoistChlorinegasNitricAcid(50Kweightconcentration)

OrganPeroxides OctylcresolOleicacidOleum~PentanePetroleum etherPhenolPropanePropylene dichloride Sulfricacid(60%weightconcentration)

Tetrahydrofurance Titaniumtetrachloride TouleneTrichloroethylene Turpentine TetralinXylenePage1of1

~~,I~v'QPP'II.