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Statistical Analysis of Straits of Mackinac Line 5: Worst Case Spill Scenarios UNIVERSITY OF MICHIGAN, ANN ARBOR DAVID J. SCHWAB, PH.D MARCH 2016

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Statistical Analysis of Straits of Mackinac Line 5: Worst Case Spill Scenarios

UNIVERSITY OF MICHIGAN, ANN ARBOR

DAVID J. SCHWAB, PH.DMARCH 2016

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University of Michigan Water Center • www.graham.umich.edu/water 1

StatisticalAnalysisofStraitsofMackinacLine5WorstCaseSpillScenarios

DavidJ.Schwab,Ph.D.

IntroductionTheStraitsofMackinacistheroughly10kmlongsectionofwaterwaythatjoinsLakesMichiganandHuronintoasinglehydraulicsystem.Itisspannedatitsnarrowestpoint(6km)bytheMackinacBridge,whichconnectsMichigan’supperandlowerpeninsulas.JustwestoftheMackinacBridge,itisalsospannedbyasubmergedsectionoftheEnbridgeInc.Line5oilpipeline.Line5typicallycarriesupto20milliongallonsoflightcrudeoil,lightsyntheticcrudeoil,andnaturalgasliquidsacrosstheStraitseachday(AlexanderandWallace,2013).CurrentsintheStraitscanbeasstrongascurrentsintheDetroitRiver(upto1m/s)andtendtoreversedirectionbetweeneastwardflowingandwestwardflowingeveryfewdays(SaylorandSloss,1976).PeakvolumetrictransportthroughtheStraitscanreach80,000m3/s(morethan10timestheflowoftheNiagaraRiver).FlowthroughtheStraitscanplayanimportantroleinwaterquality,contaminanttransport,navigation,andecologicalprocesses.Tobetterunderstandandbettercommunicatetheseuniqueflowconditions,in2014theUMWaterCenterusedarecentlypublishedhydrodynamicmodel(AndersonandSchwab,2014)oftheconnectedMichigan-Huronsystemtoproducecomputersimulationsandanimationsofhypotheticaltracer(dye)releasesintheStraits(Schwab,2014).Thesesimulationswerecarriedoutfortworeleaseperiods,oneinsummerandoneinfall.ThesimulationsshowedgraphicallyforthesetwoexamplecaseshowfarandhowfastanoilspillcouldspreadfromtheStraits.ThepurposeofthisreportistoexpandontheresultsoftheSchwab,2014studybyusingsimilarcomputersimulationtechnologytorunalargenumberofoilspillsimulationcases(840)coveringawidevarietyofweatherconditionsusingrealisticestimatesofworst-casedischargespillparameters,includingamountofoilreleased,oilcharacteristicsoflightcrudeoil(suchasspecificgravityandevaporationrate),andrealisticoilspilldispersionproperties.ThespillsimulationcasesusecurrentsfromhydrodynamicsimulationsofflowintheStraitsfor2014,basedonthesamehydrodynamiccomputermodelusedinAndersonandSchwab,2014.Theresultsofthecasesarethenanalyzedtodevelopstatisticaldistributionmapsbasedonallcasesforseveralparameters,whicharerelevantforquantitativeriskassessment.Theseincludetimeseriesoftheopenwaterareacoveredbythespill,timeseriesofthelengthofimpactedshoreline,timeseriesofthebeachedvolumeandopenwatervolume,probabilitymapsofoffshoreimpactarea,probabilitymapsofimpactedshorelinearea,andamapoftheshortesttimeitwouldtaketoreachaspecificareainanyofthe840cases.Inallcases,itisassumedthatnooiliscontainedorrecovered

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bycleanupefforts.Thisassumptionisconsistentwiththe“worstcase”scenario.Thestatisticalapproachusedhereissimilartotheapproachusedinarecentreportonthepotentialimpactofadeep-seaoilspillonthecoastsofNewZealand(LebretonandFranz,2013).HydrodynamicModelThecurrentsusedtocalculatetrajectoriesinthisstudyarebasedonthehydrodynamicmodeldescribedinAndersonandSchwab(2013).Thatmodelisathree-dimensional,unstructuredmeshhydrodynamicmodelthatextendsoverLakesMichiganandHuron,includingtheStraitsofMackinac.ThemodelisbasedontheFiniteVolumeCoastalOceanModel(FVCOM;Chenetal.,2006),afree-surface,hydrostatic,primitive-equationhydrodynamicmodelthatsolvesthecontinuity,momentum,andenergyequationsinthree-dimensionsonanunstructured,sigma-coordinate(terrain-following)mesh.TheFVCOMhasbeenvalidatedandimplementedsuccessfullyinseveralcoastaloceanapplications,aswellasintheGreatLakesandconnectingchannels(seeAndersonandSchwab,2013fornumerousreferences).Forthecombined-lakemodel,threearc-secondbathymetricandcoastlinedatafortheGreatLakeswereobtainedfromtheNOAANationalGeophysicalDataCenter(NGDC)andinterpolatedtotheunstructuredmesh.Thehorizontalgridresolutionofthemeshrangesfrom100mintheMackinacStraitsto2.5kminthecenterofthelakes.20uniformlydistributedsigmalayersprovideverticalresolution.TheAndersonandSchwabmodelwasrunusingmeteorologicalconditionsfromApril-December,2014.TherequiredsurfacemeteorologicalfieldswereextractedfromtheNOAANCEPCFSR(NationalOceanicandAtmosphericAdministration,NationalCentersforEnvironmentalPrediction,ClimateForecastSystemReanalysishttp://cfs.ncep.noaa.gov/cfsr/)hourlygriddedfieldsfor2014.ResultsofthemodelrunshowedexcellentagreementwithactualcurrentsmeasuredintheStraitsduringthisperiod(AndersonandSchwab,2016).OilSpillSimulationModelInthisstudy,anoilspillisrepresentedbyacloudofindividualtracerparticles,movingwiththecurrentsfromthehydrodynamicmodel.ThecomputercodeusedtosimulatetheparticlemotionisbasedontheLagrangianparticletrackingcodesuppliedwiththeFVCOMhydrodynamicmodel.Inthisversionoftheparticletrackingcode,wehaveoptimizedthecomputationalschemebyimprovingthealgorithmforidentifyingthemeshelementcontainingaparticularparticlelocation.Ingeneral,theparticletrackingapproachusedhereisverysimilartothewidelyusedGNOME(GeneralizedNOAAOilModelingEnvironment,http://response.restoration.noaa.gov/gnome),buthasbeenoptimizedforcarryingoutalargenumberofsimulationsbasedonasinglehydrodynamicmodelrun.Arandomwalkprocessisusedtosimulatesubgrid-scaleturbulentvariabilityinthevelocityfield.Weusedahorizontaldiffusioncoefficientof10m2/secasrecommendedforthedefaultGNOMEsetting.

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Foreachspillsimulation,theoilisrepresentedby10,000discreteparticlesreleasedonthesurfaceofthewateratapointjustsouthofhalfwaybetweenthenorthandsouthpipelineterminalsintheStraits(45.81111°N,84.76944°W).Theparticlesarereleasedatthesurfacesincethespecificgravityofthepetroleumproductscurrentlycarriedinthepipelinewouldcausetheproducttoquicklyrisetothesurfaceintheeventofapipelinebreach.WeexpectthatareleasepointnearthecenteroftheStraitsisthe“worstcase”condition,particularlyintermsofmaximizingtheareaofpotentialimpact.Threedifferentspillvolumesareconsidered:1)5,000bbl,2)10,000bbl,and3)25,000bbl.The5,000bblamountisclosetothe4,500bblvolumeusedinthemulti-agencyspillsimulationexerciseintheStraitsin2015.The10,000bblvolumeisslightlymorethanthe8,583bbl“worst-casedischargeattheStraits,”estimatedbyEnbridgeintheirresponsetotheApril,2014informationrequestfromtheStateofMichiganAttorneyGeneral.It’simportanttonotethattheestimatedamountofoilreleasedintheKalamazooRiverspillfromEnbridgeLine6Bin2010is25,000bbl.Forthethreespillvolumes—5K,10Kand25K—eachdiscreteparticleofoilinthecloudof10,000particlesinitiallyrepresents0.5,1.0,or2.5bblofoilrespectively.Thetracerparticlesinthesesimulationsarereleasedsimultaneously,buttheresultswouldnotchangesubstantiallyforreleasedurationslessthananhourortwo.Forlongerreleasedurations,thelowerreleaseratewouldlikelycauseevenmoredispersionofthespillthanthesimultaneousreleasecase.Evaporationisanimportantprocessformostoilspills.Therateofevaporationdependsprimarilyonthecompositionoftheoilproduct,andsecondarilyonenvironmentalconditions,suchastemperatureandwaves.Forthisstudy,weassumealogarithmicfunctionfortheevaporationratewithcoefficientsappropriatefor“AlbertaMixedSweetBlend”crudeoil(Fingas,2013and2015):

%Evaporation=(3.41+0.054T)ln(t)HereTistemperatureindegreesCandln(t)isthenaturallogarithmofthetimeinminutes.Weuseatemperatureof20degreesCforallsimulations.Thisresultsin32%evaporation1dayafterreleaseand40%evaporationafter10days.AlthoughwatertemperatureintheStraitsislowerthan20°Cintheearlyspringandlatefall,whichwouldslightlydecreasetheevaporationrate,itcanalsobehigherthan20°Cinthesummer,whichwouldslightlyincreasetheevaporationrate.Whencurrentsandrandom-walkdiffusioncarryaparticleintotheshoreline,theparticleisconsidered“beached”andnotallowedtomoveagain.Theamountofoiltheparticlerepresentsisitsinitialvaluereducedbyevaporation,accordingtotheequationabove.

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Spillsimulationcaseswerecarriedoutfor840overlapping60-dayperiodswithstartingdatesfromMarch31,2014andtoOctober27,2014.ThecasesendinOctobertoavoidextendingintotheStraitsicecoverseason.Littleisknownaboutthebehaviorofanoilspillunderice,sothewinterperiodwasexcludedfromthesimulations.Eachnewcasestarted6hoursafterthepreviouscase.The60daydurationofthecaseswassufficienttoestablishthemaximumextentofimpactedshorelineinallbutafewcases,andinthesecasesthelowamountandlowconcentrationofoilremaininginopenwaterafter60dayswasunlikelytocausefurthersignificantshorelineimpact.Particletrajectorieswererecordedforeachcaseandthenanalyzedstatisticallytodeveloptheprobabilitygraphsandchartsdescribedinthenextsections.SampleCasesAnimationsofparticletrajectoriesfor6ofthecaseswerecreatedtoillustratethewidevarietyofconditionsencounteredduringspring,summerandfallintheStraits.Intheanimations,theoiltracerparticlesareshownasblackdots.Amagentadotrepresentsabeachedparticle.Thelegendintheanimationindicatestheamountoftimethathaselapsedsincethebeginningofthecase,thepercentofparticlesthathavebeached,andanestimateofthelengthofshoreline,exceedingathresholdimpactlevelof12particlesperkm2.Usingadensityforlightcrudeoilof850kg/m3,forthethreereleasevolumesof5,000,10,000,and20,000bblthisimpactlevelcorrespondstoanoildensityof0.5,1.0,or2.5gm/m2respectively.Thesevaluescanbecomparedtothethresholdvaluefor“socio-economicimpactonland”of1gm/m2citedbyNOAA(2013),as“…thatamountofoilwouldconservativelytriggertheneedforshorelinecleanuponamenitybeaches.”Fingas(2015)alsosuggests1gm/m2asthethresholdforimpactstoshorelineresources.Viewthecaseanimationsonline,see:http://graham.umich.edu/news/mackinac-straits-oil-linesThestarttimesandabriefdescriptionofthe6selectedcasesfollow.• Case1:4/3/1400Z:Inthiscase,thereleasedoilformsapatchmovingwestward,away

fromtheStraitsintoLakeMichiganforalmost2dayswithoutanysignificantbeaching.After2days,waterflowintheStraitsreversesdirectionandtheoilpatchstartstomovebacktowardtheStraits.After3days,someoilhasbeguntoimpingeontheshoresfromMackinawCitywestward.Partofthepatchseparatesandcontinuestomoveeastward,eventuallyimpactingthesouthwesternshoresofBoisBlancIsland.Meanwhile,thebulkofthespillmovesbackandforththroughtheStraits,impactingtheLakeMichiganshoresofboththeUpperandLowerpeninsulaswestoftheStraits,aswellastheLowerpeninsulashoreofLakeHuroneastoftheStraits.After10days,40%oftheinitialspillisstillinthewater.ItgraduallymovesintoLakeMichiganandslowlydepositsalongthenorthernshoreasfarwestasManistiqueoverthenext30days.Inthiscase,ittookalmost25daysbefore90%oftheoilwasbeachedanditultimatelyimpactedover100kmofshoreline.

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• Case2:4/14/1400Z:Thiscaseillustrateshowquicklyaspillcouldimpactalarge

amountofshoreline.TheinitialoilpatchinthiscasemovesquicklysoutheastwardintoLakeHuronfor6hours,butthenreversesdirectionandmovesbackintothesouthernpartoftheStraitswhiledepositingoilalongthesouthernshorelinebotheastandwestofMackinawCity.After1day,morethan60%oftheoilhasbeachedandimpacted15kmofshoreline.Inthenext12hours,30%morehasbeachedand22kmofshorelinearesignificantlyaffected.

• Case3:4/16/1406Z:Thiscasestartsonly2daysaftercase2,buthasavastlydifferent

outcome.OilinitiallymovesnortheastwardtowardSt.HelenaIslandinLakeMichigan,andis90%beachedonday40when90kmofshorelineareimpacted.

• Case4:4/27/1412Z:Thisisoneofthemostextremecasesintermsofamountof

impactedshoreline.ThiscasestartssimilarlytoCase3,butafter5daystheoilpatchhasspreadtobothLakesMichiganandHuron.Bythetime90%oftheoilhasbeachedafteralmost30days,theoilhasimpacted168kmofshorelineinbothlakes.

• Case5:7/1/1406Z:Inthiscase,oilmovesalmostexclusivelyeastward,withmorethan

30%oftheoilbeachedonMackinacIsland,BoisBlancIsland,andalmosttheentireLakeHuronshorelinefromMackinawCitytoCheboyganafter3days.TheoiltravelsasfarsouthasPresqueIsleontheLakeHuronshorelinein15days,andasmallpercentageoftheparticlesreachnorthernSaginawBayonday30.ThiscasealsoillustratesthesomeofextremedistancesinLakeHuronthatcouldbereachedin30days.

• Case6:8/4/1406Z:MostoftheoilinthiscasemovesintoLakeMichigan,buta

substantialamountimpactstheshoresofMackinacIslandandSt.MartinBay.ThebulkofthespillinLakeMichiganhasimpactedtheentirenorthshoreofWildernessStateParkbyDay3.OilisbeachedonBeaverIslandonDay10,andhasreachedasfarsouthasLittleTraverseBaybyday14.Byday30,atotalof116kmofshorelinehavebeenimpacted.

StatisticalAnalysisofResults1.TimeseriesMapsoftracerparticlelocationsfromeachofthe840caseswereanalyzedateachhourafterspillinitiationtocalculate1)theopenwaterareacoveredbythespill,2)thefractionoftheinitialvolumeofoilstillinthewater,and3)thefractionoftheinitialvolumeofoilonthebeach.Atanygiventime,thevolumerepresentedby2)plus3)equalstheinitialvolumelessevaporation.

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Figures1-3showthehour-by-hourstatisticaldistributionofthesethreeparametersintermsofthemedianvalue(darkline),the25thand75thpercentiles(lightlinesborderingtheshadedarea)andthe0and100thpercentiles(bottomandtoplightlines).AsshowninFigure1,themedianvalueofopenwaterareacoveredbythespillincreasesto300km2afterabout7days,andthengraduallydecreasesasmoreoilisbeached.Themaximumopenwaterareaaffectedbyasinglespillcanreach1600km2at35days.Fiftypercentofthecaseshavemaximumopenwaterareasbetween200and400km2withthepeakoccurring5-7daysaftertheinitialrelease.AsshowninFigure2,themedianfractionofoilvolumestillonthewaterrapidlydecreasestolessthan10percentafter5days.Thelargestamountofoilremainingonthewaterafter35daysisabout10percentoftheinitialvolume.Figure3showsthatinhalfofthecases,morethan65percentoftheinitialvolumeofoilisbeachedafter7days.Inatleastonecase,70percentoftheinitialreleasevolumeisbeachedinlessthan24hours.2.OffshoreImpactThenextseriesofmapsdepictthedistributionprobabilityofoilataparticulartimeintervalafterthestartofthecase.TheareaaroundtheStraitsisdividedinto1kmx1kmsquarecellsandthepercentofcasesthathadatleastonetracerparticleinacelliscalculated.MapsareprovidedinFigures4-11forintervalsof6hours,12hours,1day,2days,4days,10days,30days,and60days.Themapsshowsthatinthefirstsixhoursaftertherelease,oilisalmostequallylikelytobefoundeastorwestoftheStraits,andcouldtravelasfaras15kmineitherdirection(Figure4).After12hours,thereisa10%chancethattheshoresofMackinacandBoisBlancIslandscouldbeaffected(Figure5).At1day(Figure6),itbecomesclearthatthereisahigherlikelihoodforoiltobefoundinLakeHuronthaninLakeMichigan,althoughitmayhavetraveledfurtherintoLakeMichigan(upto25km)thanintoLakeHuron(20km).After2days(Figure7),themostlikelylocationofoilisabout10kmeastoftheStraitswithabouthalfofthespillcasesindicatingthepresenceofoilthere.TheentireshorelinesofMackinac,BoisBlanc,andSt.HelenaIslandshavebeenimpactedinatleastoneofthecases.At4days(Figure8),themostlikelylocationtofindoilhasmovedto15kmeastoftheStraitsandover20%ofthecasesshowimpactsonMackinacIslandandBoisBlancIsland.Figures9-11showthatafter4dayssomeoilcontinuestospreadfarintoLakeHuronandtoalesserextentintoLakeMichigan,butbythistimemostoftheoilhasbeachedorevaporatedasshowninFigure2.Ananimationwascreatedofthearealprobabilitymapsathourlyintervalsforthefirst5daysafterrelease.Theanimation(availableonline,see:http://graham.umich.edu/news/mackinac-straits-oil-lines)showsthatthemostprobablelocationforoiltobefoundiscenteredintheStraitsforthefirst12hoursaftertheinitialrelease,butgraduallymovestowardthesouthshoreofLakeHuron,southandeastofMackinacIsland,duringthenext24hours.Overthenext3days,theareawhereoilispresentinatleast20%ofthespillcasesextendstothenorthofMackinacIsland,reaches15-20kmwestintoLakeMichigan,andhasmovedasfarsouthasCheboyganinLakeHuron.

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Figure12andTable1showsthepercentofcasesinwhichoilreachedaparticularareaatanytimeduringthe60-daydurationofthecaseandFigure13depictstheshortesttime(upto10days)thatitwouldtakeoiltoreachanareainanyofthe840spillcases.AsshowninTable1,over15%ofLakeMichigan’sopenwater(9,141km2)andalmost60%ofLakeHuron’sopenwater(35,264km2)couldbeaffectedbyvisibleoilfromaspillintheStraits.Atleast60%ofthecasesaffectedanareaof207km2inLakeMichiganand1,953km2inLakeHuron.Table1.Offshoreareaaffectedbyanycase.Firstcolumnisthepercentagerangeofcases,whichaffectedthisarea.SeeFigure12forgraphicalrepresentation.Percentofcases

Totalarea(km2) L.Michiganarea(km2) L.Huronarea(km2)

>0% 44,405 9,141 35,264>20% 12,931 1,688 11,243>40% 5,684 518 5,166>60% 2,160 207 1,953>80% 635 64 571

3.ShorelineImpactFigures14-16showthepercentofcasesthatwouldresultintheamountofbeachedoilexceeding“socio-economicimpact”thresholdof1gm/m2alongeach1kmsectionofshoreline.Thethreefiguresarebasedoninitialreleasevolumesof25,000,10,000,and5,000bblrespectively.Thetotallengthofshorelinethatcouldbeimpactedinanyofthe840casesis1162,835,and709kmforthethreereleasevolumesrespectively.Tables2and3showtheminimumarrivaltime(fromFigure13)andpercentofcasesexceedingthe“socio-economicimpact”thresholdfortheshoreline(fromFigures14-16)atanumberofselectedlocationsalongtheshorelinesnorthandsouthoftheStraitsforthethreeinitialreleasevolumes.

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Table2.Minimumarrivaltime(ColumnA)andpercentofcasesexceedingthe“socio-economicimpact”thresholdforshoreline(ColumnsB,C,andDcorrespondingtoinitialreleasevolumesof25,000,10,000,and5,000bblrespectively)forselectedlocationsalongtheshorenorthoftheStraits.

NorthShore A B C DGardenPeninsula 29days 1 <1 <1Manistique 27days 2 1 <1SeulChoixPoint 14.5days 5 3 1Naubinway 6days 10 5 3Brevort 40hrs 25 20 16PointAuxChenes 18hrs 40 32 30St.HelenaIsland 6hrs 58 52 50GrosCap 6hrs 60 56 54PointLaBarbre 5hrs 80 65 60BridgeViewPark 5hrs 74 57 56GrahamPoint 10hrs 75 70 67St.IgnaceFerryDocks 15hrs 50 38 35CastleRockCampground 20hrs 40 25 10MackinacIslandSouthShore 9hrs 90 85 80MackinacIslandNorthShore 12hrs 60 48 45RoundIsland 8hrs 92 88 85BoisBlancIslandSouthShore 10hrs 90 85 82BoisBlancIslandNorthShore 12hrs 70 65 60HorseshoeBay 24hrs 20 12 10SaintMartinBay 30hrs 10 6 5MarquetteIsland 51hrs 20 10 7DeTourStatePark 8days 2 1 <1DrummondIsland 9days 2 <1 <1CockburnIsland 12.5days 1 <1 <1ManitoulinIslandSWShore 14.5days 1 <1 <1

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Table3.Minimumarrivaltime(ColumnA)andpercentofcasesexceedingthe“socio-economicimpact”thresholdforshoreline(ColumnsB,C,andDcorrespondingtoinitialreleasevolumesof25,000,10,000,and5,000bblrespectively)forselectedlocationsalongtheshoresouthoftheStraits.

SouthShore A B C DCharlevoix 11days 1 1 <1Petoskey/HarborSprings 10days 1 1 <1BeaverIsland 9days 2 1 1CrossVillage 4.5days 10 5 2SturgeonBay 4days 8 5 2WaugashanceIsland 30hrs 20 16 14WildernessStateParkNorthShore 10hrs 35 30 29TheHeadlands 2.5hrs 75 70 66OldMackinacPoint 2.5hrs 92 85 82MackinawCityFerryDocks 3.5hrs 85 80 74CadottesPoint 6hrs 90 80 75PointNipigon 15hrs 85 78 72Cheboygan 30hrs 65 50 40HammondBay 3days 30 20 10RogersCity 6days 25 20 13PresqueIsle 7days 20 10 5ThunderBay 10days 5 2 1Harrisville 21days 1 <1 <1OscodaTwp. 27days 1 <1 <1AuSablePoint 29days 1 <1 <1Theshortestarrivaltimesare2.5hoursonthesouthshoreoftheStraitsnearMackinawCity,and5hoursonthenorthshore.ThesetimeswouldbereducediftheoilreleasewereclosertothenorthorsouthshorethanthereleasepointusedinthesimulationsnearthemidpointoftheStraits.MackinacIslandcouldbeimpactedinaslittleas9hours,RoundIslandin8hours,andBoisBlancIslandin10hours.LocationsthatcouldbeaffectedinlessthanadayextendfromPointAuxChenestoHorseshoeBaynorthoftheStraitsandfromthenorthshoreofWildernessStateParktoapointnorthwestofCheboyganonthesouthsideoftheStraits.SignificantshorelineimpactcouldstilloccurasfarawayastheGardenPeninsulaandCharlevoixinLakeMichigan,andthewesternendofManitoulinIslandandAuSablePointinLakeHuron.Atleast20percentofthecasesusinga25,000bblinitialdischargeshowedsignificantshorelineimpactatpointsfromBrevortinLakeMichigantoHorseshoeBayinLakeHuronalongthenorthsideoftheStraits,andfromWaugashanceIslandinLakeMichigantoPresqueIsleinLakeHuronalongthesouthsideoftheStraits.Figures17-19showthestatisticaldistributionoftheamountofimpactedshorelineasafunctionoftimeaftertheinitialreleaseforthethreeinitialvolumesof25,000,10,000,and

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5,000bbl.Themedianvalueisshownasadarkline;lightlinesborderingtheshadedareabelowandabovethemedianrepresentthe25thand75thpercentiles;andthebottomandtoplightlinesarethe0and100thpercentiles.Table4isasummaryofthelengthofimpactedshorelineforthethreedifferentinitialreleasevolumesintermsof1)thelengthofshorelinethatcouldbeimpactedbyanyspill,2)themaximumlengthofimpactedshorelineinasinglecase,and3)themedianlengthofimpactedshorelinefromallcases.Table4.Length(km)ofimpactedshorelineforthreeinitialreleasevolumesInitialrelease

volumeAllCases SingleCase MedianCase

25,000bbl 1162 245 12010,000bbl 835 170 855,000bbl 709 115 60

ConclusionsandsuggestionsforfutureworkThemainconclusionofthisreportisthataquantitativeanalysisof840oilspillcasesintheStraitsofMackinacusinga“worst-casedischarge”fromLine5showsthatmorethan1,000kmofLakeHuron-MichiganshorelineandspecificislandsarepotentiallyvulnerabletoanoilreleaseintheStraits.Thisconclusionstronglysupportstheassertionthatundertherightweatherconditions,aspillintheStraitscouldaffectasignificantamountofshorelineandopenwaterareaineitherLakeMichiganorLakeHuroninaveryshorttime.Inthecaseofa10,000bblrelease,themedianlengthofimpactedshorelinefromall840casesis85km.Threequartersofallcasesimpactedmorethan65kmofshoreline.ThemediansizeofanoilpatchfromareleaseintheStraitswas300km2after7days.Threequartersofthe840casesresultedinmaximumopenwateroilpatchsizesgreaterthan200km2afteraslittleas5days.Themaximumopenwaterareasubjecttooilinginanyofthecaseswasover1600km2.LimitationsoftheReportandResultsTheaffectoficecoverintheStraitswasnotconsidered.IcetypicallyaffectstheStraitseachwinterfromlateDecembertoApril.CommercialvesseltrafficcontinuesduringatleastpartofthisperiodwithassistancefromU.S.CoastGuardicebreakingoperations.ThepossibilityofanoilspillfromLine5alsocontinuesthroughwinter,butlittleisknownabouthowicecoverwouldaffectanoilspillintheStraits.Thisisanareathatrequiresfurtherinvestigation.OnedifferencebetweenthespillsimulationscarriedoutinthisstudyandthemethodologyusedinGNOMEisthattheGNOMEsoftwareincludesaprovisionfora“minimumregret”

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solutionbasedonuncertaintyintheassumedwatercurrents.Wedidnotincludethisfactorinourcalculations.Ifitwereincluded,the“minimumregret”solutionswouldtendtoencompasswideropenlakeareasandincreasetheamountofimpactedshoreline,sotheresultspresentedinthisreportcanbeconsideredsomewhatconservative.Thedirectaffectofwindonthespilltrajectorywasnotconsidered.Includingthisaffectwouldlikelyincreasetheaffectedopenlakeareaandamountofimpactedshoreline.Sotheresultswepresentareconservativeinthisrespect.Finally,wehavenotconsideredprocessesbywhichoilwouldsinkorbeotherwiseincorporatedintothewatercolumnbelowthesurface.ForthetypeofpetroleumproductsbeingcarriedbyLine5,thiseffectwouldprobablybesmall,butinanycase,ourfindingswouldstillapplytooilremainingonornearthesurface.Theresultsfromthisreportareanticipatedtoprovideguidelinesforthedevelopmentofafullriskanalysisinthefuture.RecommendationsforFurtherStudyThespillscenariosimulationsinthisstudyareonlythefirststepinacompleteriskanalysisofa“worstcasedischarge”ascalledforintheStateofMichiganPetroleumPipelineTaskForceReport(2015).Otherconsiderationsinamorecompleteriskanalysiswouldinclude1)analysisofenvironmentalimpacts,2)cleanupcosts,3)restorationandremediationmeasures,4)anaturalresourcedamageassessment,and5)Economicdamagetopublicandprivatesectorinterests.Inaddition,informationabouthowicecoverwouldaffectanoilspillintheStraitsrequiresfurtherinvestigation.AcknowledgementSupportedbytheNationalWildlifeFederation,GreatLakesRegionalCenter

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References:Alexander,J.andB.Wallace,2013.Sunkenhazard:AgingoilpipelinesbeneaththeStraitsofMackinacanever-presentthreattotheGreatLakes.NationalWildlifeFederation:17pp.(http://www.nwf.org/pdf/Great-Lakes/NWF_SunkenHazard.pdf)Anderson,E.J.,andD.J.Schwab,2013.Predictingtheoscillatingbi-directionalexchangeflowintheStraitsofMackinac.JournalofGreatLakesResearch39(4):9pp.(DOI:10.1016/j.jglr.2013.09.001).(http://www.glerl.noaa.gov/pubs/fulltext/2013/20130038.pdf)Anderson,E.J.,andD.J.Schwab,2016.SummertimeGeostrophicFlowintheStraitsofMackinac(inpreparation).Beegle-Krause,J.,2001.GeneralNOAAOilModelingEnvironment(GNOME):anewspilltrajectorymodel.2001,pp.865--871.Chen,C.,Beardsley,R.C.,Cowles,G.Anunstructuredgrid,finite-volumecoastaloceanmodel(FVCOM)system.Oceanography19,78–89.(2006)Fingas,M.,2015.HandbookofOilSpillScienceandTechnology(edM.Fingas),JohnWiley&Sons,Inc.,Hoboken,NJ.doi:DOI:10.1002/9781118989982

Fingas,M.F.,2013.ModelingOilandPetroleumEvaporation.J.PetroleumScienceResearch,2:3,104-115.

Lebreton,L.C.-M.andFranz,T.2013.TrajectoryAnalysisOfDeepSeaOilSpillScenariosInNewZealandWaters.ReportpreparedforGreenpeaceNewZealand,Greenpeace,73pp(http://www.greenpeace.org/new-zealand/en/reports/New-Zealand-Oil-Spill-Report/)

MichiganPetroleumPipelineTaskForceReport,2015.(https://www.michigan.gov/documents/deq/M_Petroleum_Pipeline_Report_2015-10_reducedsize_494297_7.pdf)

NOAA,2013.ScreeningLevelRiskAssessmentPackage-BunkerHill.(http://sanctuaries.noaa.gov/protect/ppw/pdfs/bunker_hill.pdf)

Saylor,J.H.,Sloss,P.W.,1976.WatervolumetransportandoscillatorycurrentflowthroughtheStraitsofMackinac.J.Phys.Oceanogr.6,229–237.

Schwab,D.J.,2014.StraitsofMackinacContaminantReleaseScenarios:FlowVisualizationandTracerSimulations.U-MWaterCenterResearchReport,7pp.(http://graham.umich.edu/water/news/mackinac-straits-contaminant-scenarios)

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FiguresFigure1.Timeseriesofstatisticaldistributionofaffectedopenwaterareaineachofthe840spillcases.Thedarklineisthemedianvalue,thelightlinesborderingtheshadedareaarethe25thand75thpercentiles,andthelowerandupperlinesarethe0thand100thpercentiles.Figure2.Timeseriesofstatisticaldistributionoffractionofinitialoilreleasevolumeremainingonwaterineachofthe840spillcases.Thedarklineisthemedianvalue,thelightlinesborderingtheshadedareaarethe25thand75thpercentiles,andthelowerandupperlinesarethe0thand100thpercentiles.Figure3.Timeseriesofstatisticaldistributionfractionofinitialreleasevolumethathasbeachedineachofthe840spillcases.Thedarklineisthemedianvalue,thelightlinesborderingtheshadedareaarethe25thand75thpercentiles,andthelowerandupperlinesarethe0thand100thpercentiles.

0 20 40 60Days after Release

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Figure4.Probabilityofpresenceofoil(percentofcases)at6hoursafterinitialrelease.

Figure5.Probabilityofpresenceofoil(percentofcases)at12hoursafterinitialrelease.

Probability at 6 hours

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Figure6.Probabilityofpresenceofoil(percentofcases)at1dayafterinitialrelease.

Figure7.Probabilityofpresenceofoil(percentofcases)at2daysafterinitialrelease.

Probability at 1 day

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Figure8.Probabilityofpresenceofoil(percentofcases)at4daysafterinitialrelease.

Figure9.Probabilityofpresenceofoil(percentofcases)at10daysafterinitialrelease.

Probability at 4 days

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Figure10.Probabilityofpresenceofoil(percentofcases)at30daysafterinitialrelease.

Figure11.Probabilityofpresenceofoil(percentofcases)at60daysafterinitialrelease.

Probability at 30 days

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Figure12.Percentofcasesinwhichoilispresentatanytimeafterinitialrelease.

Figure13.Minimumtraveltime(upto10days)toalocationfromanycase.

Percent of Cases

> 0%20 %40 %60 %80 %100 %

0 50

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Travel time

1 day2 days5 days10 days

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Figure14.Probability(percentofcases)thatbeachedoilconcentrationexceeds1gm/m2after60daysfromanyspillcase,basedonaninitialreleasevolumeof25,000bbl.

Figure15.Probability(percentofcases)thatbeachedoilconcentrationexceeds1gm/m2after60daysfromanyspillcase,basedonaninitialreleasevolumeof10,000bbl.

25,000 bblTotal length 1162 km

> 0%20 %40 %60 %80 %100 %

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10,000 bblTotal length 835 km

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Figure16.Probability(percentofcases)thatbeachedoilconcentrationexceeds1gm/m2after60daysfromanyspillcase,basedonaninitialreleasevolumeof5,000bbl.

Figure17.Timeseriesofstatisticaldistributionoflengthofimpactedshorelinebasedonaninitialreleasevolumeof25,000bbl.Thedarklineisthemedianvalue,thelightlinesborderingtheshadedareaarethe25thand75thpercentiles,andthelowerandupperlinesarethe0thand100thpercentiles.

5,000 bblTotal length 709 km

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Figure18.Timeseriesofstatisticaldistributionoflengthofimpactedshorelinebasedonaninitialreleasevolumeof10,000bbl.Thedarklineisthemedianvalue,thelightlinesborderingtheshadedareaarethe25thand75thpercentiles,andthelowerandupperlinesarethe0thand100thpercentiles.Figure19.Timeseriesofstatisticaldistributionoflengthofimpactedshorelinebasedonaninitialreleasevolumeof5,000bbl.Thedarklineisthemedianvalue,thelightlinesborderingtheshadedareaarethe25thand75thpercentiles,andthelowerandupperlinesarethe0thand100thpercentiles.

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The Water Center engages researchers, practitioners, policymakers, and nonprofit groups to support, integrate, and improve current and future freshwater restoration and protection efforts. The Water Center conducts collaborative science, supporting Great Lakes restoration and coordinates the National Estuarine Research Reserve System (NERRS) Science Collaborative. The Water Center is part of the U-M Graham Sustainability Institute, which fosters sustainability through translational knowledge, transformative learning, and institutional leadership.

UNIVERSITY OF MICHIGAN BOARD OF REGENTSMichael J. Behm, Grand Blanc; Mark J. Berstein, Ann Arbor; Laurence B. Deitch, Bloomfield Hills; Shauna Ryder Diggs, Grosse Pointe; Denis Ilitch, Bingham Farms; Andrea Fischer Newman, Ann Arbor; Andrew C. Richner, Grosse Pointe Park; Katherine E. White, Ann Arbor; Mark S. Schlissel, ex officio