The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend...

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The Arctic Species Trend Index

Transcript of The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend...

Page 1: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

CAFF Assessment Series No. 7April 2012

The Arctic Species Trend IndexTracking trends in Arctic marine populations

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CAFF Designated Agencies:

• DirectorateforNatureManagement,Trondheim,Norway

• EnvironmentCanada,Ottawa,Canada

• FaroeseMuseumofNaturalHistory,Tórshavn,FaroeIslands(KingdomofDenmark)

• FinnishMinistryoftheEnvironment,Helsinki,Finland

• IcelandicInstituteofNaturalHistory,Reykjavik,Iceland

• TheMinistryofDomesticAffairs,NatureandEnvironment,GovernmentofGreenland

• RussianFederationMinistryofNaturalResources,Moscow,Russia

• SwedishEnvironmentalProtectionAgency,Stockholm,Sweden

• UnitedStatesDepartmentoftheInterior,FishandWildlifeService,Anchorage,Alaska

CAFF Permanent Participant Organisations:

• AleutInternationalAssociation(AIA)

• ArcticAthabaskanCouncil(AAC)

• Gwich’inCouncilInternational(GCI)

• InuitCircumpolarCouncil(ICC)

• RussianIndigenousPeoplesoftheNorth(RAIPON)

• SaamiCouncil

Thispublicationshouldbecitedas:McRae,L.,Deinet,S.,Gill,M.&Collen,B.(2012)TrackingTrendsinArcticmarinepopulations.CAFFAssessmentSeriesNo.7.ConservationofArcticFloraandFauna,Iceland.ISBN:978-9935-431-15-8

Frontcoverphoto:neelsky/Shutterstock.com

Backcoverphoto:SergeyUryadnikov/Shutterstock.com

Graphicsby:MargrétValmundsdóttir

Formoreinformationpleasecontact:CAFF International SecretariatBorgir, Nordurslod600 Akureyri, IcelandPhone: +354 462-3350Fax: +354 462-3390Email: [email protected]: http://www.caff.is

Editing:JoanEamer,DonRussellLayout:CourtneyPrice

Acknowledgements

___CAFFDesignatedArea

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Table of Contents

Executive Summary ................................................................................................................................ 5

Introduction ............................................................................................................................................ 6

Results and Discussion ........................................................................................................................... 7

Pan-Arctic update .................................................................................................................................................. 7Table1.NumberofspeciesandpopulationsintheASTI........................................................................................................... 7Figure1.Datacoveragebytaxonomicclass................................................................................................................................... 7Figure2.Indexofabundancefor323Arcticvertebratespecies(890populations),from1970to2007.................. 8Figure3:IndexofabundanceforArcticvertebratespeciesfrom1970to2007groupedbyhigh,lowandsubArctic.............................................................................................................................................................................................................. 8

Marine results ......................................................................................................................................... 9

Overview ................................................................................................................................................................ 9Figure4.Spatialdistributionofmarinepopulationdatacollected......................................................................................... 9Table2.NumberofArcticmarinespeciesandpopulationsbyoceanbasinandclass..................................................10Figure5.IndicesofabundanceforArcticvertebratespecies,groupedbymarineandterrestrialspecies,1970to2005..............................................................................................................................................................................................10

Baselines .............................................................................................................................................................. 11Figure6.Indicesofabundancebytaxonomicclass,1970to2005.......................................................................................12Figure7.Effectsoftheremovalofeachclassonthemarineindicesofabundanceweightedatthespecieslevel..............................................................................................................................................................................................................12

Taxonomic trends ................................................................................................................................................ 12

Regional trends ................................................................................................................................................... 14Figure8.Indicesofabundancebyoceanregion,1970to2005............................................................................................15Figure9.Boxplotshowingthemedianannualrateofchangeoffishspeciesineachoceanicregionfrom1970to2005.............................................................................................................................................................................................15

Bering Sea effect .................................................................................................................................................. 16Figure10.IndicesofabundanceformarinepopulationsshowingtheeffectofremovingtheBeringSeaandAleutianIslandpopulations.BSAIdatasetscomprised71species,138populations..................................................16Figure11.IndicesofabundanceformarinepopulationsfromtheBeringSeaandAleutianIslandregion(BSAI)forbirds,fishesandmammals...............................................................................................................................................17

Ecological trends ................................................................................................................................................. 18

Sea-ice association .............................................................................................................................................. 18Figure12:Knownstatusofindividualpopulationsforninesea-iceassociatedmarinespecies...............................18

Regime shift ......................................................................................................................................................... 19Figure13.Indicesofabundanceforbenthic,pelagic,andbenthopelagicfishspeciesfrom1970to2005..........19

Pelagic fish trends ............................................................................................................................................... 20Figure14.ComparisonofthethreeyearrunningaverageforthepelagicfishindexandtheArcticOscillation..................................................................................................................................................................................................20Figure15.ComparisonofestimatedherringpopulationsizeintheBristolBayareaandtheseaiceextentintheEastBeringSea............................................................................................................................................................................21

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Figure16.Boxplotshowingmedianrateofchangebytrophiclevelforparasitesandforprimary,secondary,andtertiaryconsumers.........................................................................................................................................................................22Figure17.Trendsinabundanceindicesforspeciesofpiscivorousandplanktivorousbirdsandfishesfrom1970to2005.............................................................................................................................................................................................22

Trophic level ......................................................................................................................................................... 22

Conservation management trends .................................................................................................................... 23Figure18.Indicesofabundanceforpopulationsbythreatclassificationfrom1970to2005....................................23Table3.Totalnumbersofpopulationsandspeciesthatarefoundinsideandoutsideprotectedareas................24Figure19.Boxplotshowingthemedianratesofchangeofbirdpopulationsforwhichathreatisidentified,groupedbyprimarythreat,1970to2005......................................................................................................................................24

Protected areas .................................................................................................................................................... 24Figure20.Indicesofabundanceforprotectedandunprotectedbirdpopulationsfrom1970to2005.................25

Acknowledgements .............................................................................................................................. 26

References ............................................................................................................................................. 27

Appendix 1: Methods ........................................................................................................................... 31Populationdata..........................................................................................................................................................................31Datatagging...............................................................................................................................................................................31

AppendixTable1-A.Datatypeofpopulationsbyclass...........................................................................................................31AppendixTable1-B.Populationandspecies-baseddatatags..............................................................................................32

Trendanalysis.............................................................................................................................................................................32

Appendix 2: Table of ANOVA results ................................................................................................... 33

Appendix 3: List of monitored species and locations ........................................................................ 34

Appendix 4: Table of index values ...................................................................................................... 45

Appendix 5: Table of population trends for nine sea-ice associated species .................................. 50

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Executive Summary

Duetothecomplextemporaldynamicsofwildlifepopulationsandfishstocks,long-termmonitoringdatameasuringchangeinpopulationtrendsisanecessaryandrevealingwaytotracktheeffectofenvironmentalchangesonwildlife.

TheArcticSpeciesTrendIndex(ASTI)tracksthetemporalabundancein890populationsof323vertebratespecies.Thisrepresentsanupdateoftheindexfirstreportedonin2010(McRaeet al.2010)andshowsthataveragespeciespopulationabundanceintheArctichasincreasedoverthetimeperiodbetween1970and2007.Thispattern,however,isnotconsistentamongregionsasvertebrateabundancehasincreasedonaverageinthelowArcticbutnotinthehighArcticandsubArctic.ThemarinecomponentoftheASTIshowsagreaterincrease–andevidenceispresentedthatthetrendsinmarinespeciesaredrivingthepan-Arcticindex.Themarinetrendvariesaccordingtotaxonomicclassandoceanbasin,amongothervariables.

Marinemammalpopulationsincreasedonaveragebutthereisaneedtointerprettherecoveryinnumbersinthecontextofthe1970baseline,assomepopulationsstillremainheavilydepletedafterhistoricaloverexploitation.RecentdeclineswereobservedintheBeringSeaandAleutianIslandsforsevenspecies:belugawhale,Stellersealion,harbourseal,seaotter,Pacificwalrus,northernfurseal,andgraywhale.Thereasonsforthepopulationdeclinesarenotuniformforallspecies;theassociatedthreatsincludeoverharvesting,increasedpredation,lossofsummerseaice,anddepletedpreyresource.

MarinebirdindicesshoweitherstableordecliningtrendsdependingontheArcticregioninquestion.Climatechange,exploitation,andinvasivespeciesareanthropogenicthreatsthathavebeenlinkedwithnegativetrendsforsomeofthesepopulations—buttheremayalsobeaninfluencefromnaturalchangesinenvironmentalandforagingconditions,especiallyaffectingpiscivorousspecies,particularlyintheBeringSeaandAleutianIslands.

ThefishdatasetwasdominatedlargelybybenthicandcommerciallyfishedspeciesfromtheBeringSea.AmongfishpopulationstherewereincreasesinthePacificandArcticbasinsofthestudyarea,possiblyduetoincreasesinseasurfacetemperaturesobservedinregionssuchastheBeringSeainthe1970sand1980s.TheaveragetrendinsevenpelagicfishspeciesshowedavariablepatternandwasfoundtohaveastrongassociationwithsimilartrendsintheArcticOscillation.

Populationsthatwereaffectedbyatleastoneanthropogenicthreatshowedanoverallincreasingtrendfrom1970to2005–buttheupwardtrendwasduetoincreasesinabundancethatoccurredinthefirst15yearsofthatperiod.Incontrast,populationsnotidentifiedasbeingunderthreatincreasedfour-foldoverthe35-yearperiod.

Forbirdpopulations,therewasadifferenceintrenddependingonwhetherthepopulationwaslocatedinsideoroutsideaprotectedarea.Onaveragethoseoutsideprotectedareasdeclinedslightlyinabundance,whichcouldbedueinparttounsustainableharvestingofseabirdsinsomelocations,butmoreinformationisneededinordertotestthismorefully.

ThemarinedatasetisdominatedbyfishspeciesandbypopulationsfromtheBeringSeawhich,attimes,havealargeinfluenceonsomeofthesub-indices.ThecurrentspatialextentofmonitoringneedstobeimprovedtobetterrepresentregionsandspeciesclassesacrossthemarineArctic.

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Introduction

TheArcticisoneoftheregionsintheworldexperiencingthemostrapidvisibleandmeasurablechangesinitsclimateandenvironment(ACIA2005;Stroeveet al.2007).Asagloballyimportantareaforbiodiversity,itisvitalthataccuratewildlifemonitoringsystemsareinplacetomeasurehowspeciesintheArcticarereactingbothspatiallyandtemporallytodifferenttypesandmagnitudesofpressure.

Evaluatingtrendsinspeciesabundanceisoneofthemostrevealingwaystoexaminebroad-scalepatternsofbiodiversitychange.TheArcticSpeciesTrendIndex(ASTI),developedforthispurpose,usespopulationtimeseriestrenddatafromvertebratespeciesfrom1970untilthepresentday.ThefirstreportonArcticspeciestrends(McRaeet al.2010;www.asti.is)revealedthattrendsinArcticvertebratesshowanoverallincreaseinabundanceovera34-yearperiod.Furtheranalysisrevealedthatthispatternwasnotconsistentwithinregions,systemsorgroupsofspecies.Incontrasttopatternsintheterrestrialenvironment,marinevertebratepopulationsfromthisregionshowincreasingtrendsinabundanceonaveragesince1970(McRaeet al.2010).Althoughthistrendslowedinratefrom1986,theoverallresultsuggeststhatby2004a53%increaseinabundanceofArcticmarinevertebrateshadoccurredcomparedtoabaselineyearof1970.DisaggregationofthemarinedatasetintotaxonomicandregionalresultsacrosstheArcticindicatethattheremaybedisparityinabundancetrends(McRaeet al.2010).

Oneoftheprincipalweaknessesofrelyingonanon-stratifiedmonitoringnetwork,whichmustbeovercometoprovidethebestpossibleindicatorsofaggregatedpopulationtrend,isthedominanceofparticulardatasetsduetotheimbalanceinmonitoringfocus(e.g.,moremonitoringofcommerciallyexploitedspecies)andtheimbalanceindistributionofmonitoringsites(Bohmet al.2012).ThemarinecomponentoftheASTIdataset,forexample,issomewhatdominatedbypopulationtimeseriesofincreasingtrendfromtheBeringSeaandAleutianIslands.Itislikelythatspeciesfromtheselocationsaredrivingthemarineandthepan-Arcticindexwhilstmaskingotherimportanttrends.

TheimportanceofobtainingaclearpictureandimprovingunderstandingofbiodiversitytrendsintheArcticmarineenvironmentcannotbeoverstated.AwealthofresearchintoenvironmentalpatternsintheArcticmarineenvironmentoverrecentyearshasbroughttolightchangesinmarinesystems,bothcyclicalandlong-term,andalsointeractionsamongspeciesthatoccurinthissystem.Recentresearchshows,forexample,impactsonbiodiversityofdeclinesinsea-iceextent(e.g.,Heide-Jørgensenet al.2010;Kovacset al.2010);warmingseasurfacetemperaturesinareassuchastheBeringSeaandpossibleeffectsonspecies(e.g.,Coyleet al.2007;Stabenoet al.2007;Ironset al.2008);and,trophicinteractionsandcascadesthatcanoccurasaresultofenvironmentalchangesinthemarinehabitat(e.g.,Stempniewiczet al.2007;Anthonyet al.2008).

Inlightofthesechanges,furtherinvestigationoftheunderlyingtrendsinthemarineindexarenowneededtoestablishwhethertheincreasingtrendiscommontoallmarinespeciesandregionsandalsotoputtheseresultsinthecontextofenvironmentalchangesintheArcticseas.Inordertoexplorethis,wepresentanumberofsub-indicesshowingtrendsingroupsofmarinevertebratepopulationsdisaggregatedtaxonomically,geographically,ecologically,andaccordingtodifferenttypesofconservationmanagement.Finally,variablesfromthesecategoriesweretestedinrelationtopopulationtrends,usingsingletrendvaluesbasedonthetotalrateofchangeforeachpopulation.Thisgaveustheoptiontolookforsignificantfactorsinpredictingmarinepopulationtrends(seeAppendix1:Methodsfordetails).

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Results and Discussion

Pan-Arctic update

Followingdatacollection,timeseriesupdates,andremovalofredundantdatasets,theASTIwasupdatedtocover323speciesmonitoredthrough890populations(Table1).Thisisanadditionof17speciessincethefirstASTIreport(McRaeet al.2010),increasingtherepresentationofArcticvertebratespeciesfrom35%to37%(Figure1).Notethatapopulation,forthepurposesoftheASTI,isdefinedbyadatasetofannualmeasuresofabundanceofonespeciesfromaspecificlocation.

Species Populations

Mammals Birds Fishes Total Mammals Birds Fishes Total

Terrestrial 30 132 - 162 182 256 - 438

Freshwater 1 44 14 59 3 64 75 142

Marine 22 34 55 111 60 152 98 310

Total (unique species) 53 201 69 323 245 472 173 890

DuetoalargenumberofdataupdateswewereabletoextendtheoriginalASTIbyanotherthreeyearstocovertheperiod1970to2007(the2010ASTIincludeddataonlyto2004).Thisshowsthattherelativelystabletrendatthepan-Arcticlevelthatwasevidentin2004continueduntil2007.PlottingASTIvaluesoverthefulltimeperiod(Figure2)showsthatvertebrateabundancetrendsincreasedfrom1970until1990whentheindexstabilised,remainingaroundthe1.2indexvaluelevel(20%abovethebaseline)fortherestofthetimeseries.

HighArcticspeciesdeclinedfrom1970tothemid-1990sandthenremainedfairlystable(Figure3);lowArcticspeciesaccountformostoftheoverallincreaseinabundanceinthefirsttwodecades,withthetrendlevellingoffinthemid-1990s.SubArcticspeciesincreasedfrom1970tothemid-1980sandthendeclinedatasteadyrate.ThethreeyearsofdataaddedinthisupdateoftheASTI(2005to2007)showmarkeddifferencestotheprecedingfewyears:adownwardtrendforlowArcticspeciesandanupward

Table1.NumberofspeciesandpopulationsintheASTITheupdatedASTIcoversatimeperiodof1970to2007.

Figure1.Datacoveragebytaxonomicclass.

BlackbarsrepresenttheproportionofArcticspeciesforeachclassforwhichpopulationdataareavailable

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trendforhighArcticspecies.Thesechangescanceleachotheroutwhenallspeciesarecombined(Figure2).ThisistooshortatimetointerpretasasignificantchangeandpointsouttheimportanceoffrequentupdatesoftheASTI.

Figure2.Indexofabundancefor323Arcticvertebratespecies(890populations),from1970to2007.Thefigureplotsthe95%confidenceintervalsandthenumberofpopulationscontributingtoeachyearoftheindex*.The2007indexvalueis1.19.

*Confidenceintervalsarenotshownintheremainingfigurestomaintainclarityofthegraphs.ThevaluescanbefoundinAppendix4:Tableofindexvalues

Figure3:IndexofabundanceforArcticvertebratespeciesfrom1970to2007groupedbyhigh,lowandsubArctic.

Polar bear. Photo: Wild Arctic Pictures/Shutterstock.com

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Marine results

Overview

TheArcticmarinedatasetcontainsatotalof111speciesand310populationtimeseries(Table2)from170locations(Figure4).Speciescoverageisabout34%ofArcticmarinevertebratespecies(100%ofmammals,53%ofbirds,and27%offishes)(Bluhmet al.2011).Atthespecieslevel,eventhoughtherepresentationofArcticfishspeciesislowerthanthatofmammalsandbirds,thedataaredominatedbyfishes,primarilyfromthePacificOcean(especiallytheBeringSeaandAleutianIslands).However,therearemorepopulationtimeseriesintotalforbirdspecies,whichisreflectiveofthisgroupbeingbothbetterstudiedhistoricallyandalsomonitoredatmanysmallstudysitescomparedtofishandmarinemammalspecies,whichareregularlymonitoredatamuchlargerscalethroughstockmanagement(Table2).Notethatthetimespanselectedformarineanalysesis1970to2005(comparedwith1970to2007fortheASTIforallspecies,asdiscussedabove).

Figure4.SpatialdistributionofmarinepopulationdatacollectedThesizeofthecircledenotesthenumberofpopulationtimeseriesfromthatlocation.Forgreaterclarityinthedivisionofpopulationsbyoceanregion,theArcticOceanbasemapareausedforallanalysesisshowninpink.

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Species Populations

Mammals Birds Fishes Total Mammals Birds Fishes Total

Pacificbasin 13 22 40 75 32 59 62 153

Atlanticbasin 2 13 7 22 3 25 16 44

Arcticbasin 15 22 15 52 25 68 20 113

Total (unique species) 22 34 55 111 60 152 98 310

Populationdataspannedtheyears1950to2011.However,thegreatestcontiguousperiodofdataacrossallspeciesliesbetween1970and2005.Thisdictatedthetemporallimitssetforthemarineindex.

TheArcticmarineindex(bluelineinFigure5)showsaverysimilartrendtotheindexforallArcticvertebrates,exhibitinganincreasingtrenduntil1990andverylittlesubsequentchange.Incontrast,theindexforterrestrialvertebratespeciesshowsverydifferentpattern,withlittlechangeuptoabout1990,followedbyaslowdecline.ThissuggeststhatthemarinespeciesaredrivingtheoverallArcticindex(seealsoMcRaeet al.2010).

Figure5.IndicesofabundanceforArcticvertebratespecies,groupedbymarineandterrestrialspecies,1970to2005.

Datasetsformarine:111species,310populations

Kittewakes on sea ice. Photo: Gail Johnson/Shutterstock.com

Table2.NumberofArcticmarinespeciesandpopulationsbyoceanbasinandclassMarineanalysescoverthetimeperiod1970to2005.

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Baselines

Theconceptofbaselinesiscriticaltointerpretingananalysissuchastheonereportedhere.Currenttrendsinmarineecosystemsneedtobeinterpretedagainstasolidunderstandingofthemagnitudeanddriversofpastchanges(Lotze&Worm2009).Duetothelackofwidespreadabundancedatapre-1970,theapproachtakenhereistosetthebaselinetotheyear1970(Lohet al.2005).However,anunderstandingofthehistoricalchangesinthesystemcouldlikelyyieldadifferentinterpretationandthuscautionisneededwhenreferringtotheoverallchangeinanindexfrom1970to2005.

Forcertainpopulationsthathaveincreasedinabundancesince1970,itcanbemeaningfultoputthepositivetrendintoanhistoricalcontext.Anthropogenicthreatssuchasexploitationmayhavehadanimpactonpopulationsizebeforethistimeandhencetherecovery,althoughpositive,maynotbeequivalenttothedeclinethatoccurredpreviously.Sometechniquesarebeingdevelopedtotrytoreconstructhistoricalbaselines,specificallyformarinespecies(Lotze&Worm2009),inordertoobtainamoreaccuratepictureofaspecies’currentconservationstatusandasguidelinesforfutureecosystemrestoration.

ThisconceptisparticularlypertinenttothemarinemammalsoftheArcticastherehasbeenalongestablishedpracticeofsubsistenceandcommercialhuntingofmanyspeciesandseverepopulationreductionsofsomespeciesfromhistorical,unsustainablecommercialwhalingSomemarinemammalpopulationshaveincreaseddramatically—positivenewswhencomparingtrendsagainsta1970baselineyear.However,manypopulationsareunlikelytohaveincreasedbacktohistoricalhighs(Alteret al.2007;Lotze&Worm2009;Wadeet al.2011).Forexample,researchonEschrichtius robustus(graywhale)fromtheeasternPacificsuggestedthat,whileabundancehasincreaseddramatically,thewhaleshave,atbest,recoveredto28-56%oftheiroriginalabundancelevels(Alteret al.2007).SimilarfindingshavebeendocumentedforpopulationsofOdobenus rosmarus(Greenlandwalrus)(Witting&Born2005),thewesternArcticpopulationofbowheadwhale(Georgeet al.2004),andforthehighlycommercialGadus morhua(Atlanticcod)(Rosenberget al.2005).

Supply vessel entering Appilatoq, Greenland. Photo: Gentoo Multimedia Ltd./ Shutterstock.com

Fishing nets. Photo: jele/Shutterstock.com

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Taxonomic trends

Themarinedatasetisdominatedbyfishspecies(Table2)andaseachspeciestrendisequallyweightedwithintheindex,thismeansthatthisgroupcarriesthemostweightintheoverallindex.Acloserlookatsub-indicesofeachtaxonomicgroupsupportsthishypothesisastrendsinmarinefishincreaseduptoanindexvalueof2.6overthe35-yearperiod(Figure6).Marinemammalsalsoshowedanupwardtrend.Bothmammalandfishindicesincreasedtoamuchgreaterdegreethantheindexforbirds,whichdisplayedaslowerincreasingtrendto1984,thenremainedstable,withindicationsofaslowdeclinestartingafter1998.

Figure7showstheinfluenceofeachtaxonomicgroupbyplottingthemarineindexwiththesequentialremovalofbirds,mammals,andfishes.Mammalsareindicativeoftheoverallmarineindex—theirremovalfromtheanalysisresultsinlittlechangetothetrendline.Themagnitudeoftheinfluenceofbirdandfishtrendsappearstobelargelythesame,butinoppositedirections.Thepresenceofbirdtrendsreducestheoverallincreaseandthepresenceoffishtrendsraisesit.

Figure6.Indicesofabundancebytaxonomicclass,1970to2005.Indicesareaveragedforbirds(34species,152populations),fishes(55species,98populations),andmammals(22species,60populations).

Figure7.Effectsoftheremovalofeachclassonthemarineindicesofabundanceweightedatthespecieslevel.

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Overall,thetaxonomicresultssuggestthattherehasbeenanaverageincreaseinabundanceamongstArcticmammalspecies.Oneexplanationisthattheyhaveincreasedinabundanceoverthistimeperiodfollowingsharpdeclinesrelatedtohistoricaloverharvesting(seediscussiononthispointinBaselinesectionabove).MammalspeciesincreasedinabundanceinallthreeregionsofthemarineArctic—Pacific,Arctic,andAtlantic(resultsoftheanalysisgroupedbyoceanregionnotdisplayed).MarinemammalpopulationtrendsareillustratedinmoredepthwhenwefocustheanalysisontheBeringSeaandAleutianIslandregionaspartoftheregionaltrendssection.

Marinebirdpopulationshavenotincreasedbythesamemagnitudeasmammalsandfishes(Figure6).Theincreaseinbirdabundancestabilisesaround1984andin1998startsshowingadecline.Theoverallpicturesuggeststhattheabundanceofmarinebirdswasgreaterin2005comparedto1970butwaslesserthanthatin1998.Thisrecenttrendmayindicatethestartofalongertermdeclinesoitwillbeimportanttomonitorthisoverthecomingyearsandtoinvestigatewhatmaybedrivingthesetrends.

Recentstudieshaveshownthatpopulationtrendsinsomebirdspeciesmaybeinfluencedbychangesinclimateandsea-iceextent,astheseenvironmentalconditionsdictatetheavailabilityoffoodandthereforebirdabundance,whichcanhavesubsequentindirecteffectsonthecompositionoftheterrestrialcoastalenvironment(e.g.,Stempniewiczet al.2007).Forexample,somepopulationdeclinesresearchershaveobservedinpiscivorousseabirdsarethoughttobeduetochangesinforagingconditionsdeterminedbywintersea-ice(Byrdet al.2008)andalinkhasbeenestablishedbetweenchangesinsea-surfacetemperatureacrosstheArcticanddeclinesinseabirdcolonyproductivity(Ironset al.2008).Thisisdiscussedfurtherintheecologicaltrendssectionaspartoftheanalysisontrophiclevel.

Marinefishshowalargeoverallincreaseinabundancewhichpredominantlyoccurredinthe20-yearperiodbetween1970and1990(Figure6).Thetrendsinfishspeciesarecontributingmoretothepositivetrendinthemarineindexthantheothertwoclasses(Figure7),sotheseresultsstronglysuggestthatanoverallincreaseinfishabundanceoccurredoverthe35-yearperiod.

Identifyingthedriversbehindthischangeinabundanceiscomplexasthedatasetcomprisesabroadrangeofspeciesthatcouldberespondingdifferentlytovaryingdegreesofclimatic,ecological,and

Guillemots. Photo: Ewan Chesser/Shutterstock.com

Fish feeding on zooplankton. Photo: Mareano Institute of Marine Research

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managementpressures.Commercialexploitationisamoreimportantfactorinfishpopulations(moresothanformostbirdandmammalpopulations),withalittleoverhalfthefishspeciesinthisdatasetbeingcommerciallyexploited.Thefishdatasetcontainsalargenumberofbenthicspecies(two-thirdsofthepopulations).Thismeansthatthedatasetforfishissomewhatdominatedbytheinfluenceofcommercialexploitationandtheemphasisonbenthicfishes.

Populationtrendsarenotnoticeablydifferentaccordingtoaspectsoffishecologysuchastrophiclevelandhabitat(seeEcologicaltrendssection).Finally,regionaldifferenceswerenoticeableinfishpopulationtrends,mostnoticeablyintheAtlanticOceanwheretheaveragechangewasacontinuedandunabateddecline(Appendix4:Tableofindexvalues).Thispatternisalsoevidentintheregionaldisaggregationoftheentiremarineindex,theunderlyingtrendsofwhicharediscussedinthefollowingsection.

Regional trends

Threeregions:weredefinedPacific,Arctic,andAtlantic(seeFigure4forboundaries)toevaluateregionaltrendsinmarinepopulationabundance.Theseregionsvaryaccordingtoecologicalprocessesanddifferentmanagementandpoliticalpressures.

Bird,mammal,andfishtrendsineachoftheseregionswereexaminedinordertohelpinterprettheresultswefound.Theresultsoftaxonomicanalysesforeachregiondidnotproducereliableindices,largelyduetothesmallsizeofeachdataset,sotheyhavenotbeenincludedinthisreport.However,theinfluenceofbirds,mammalsandfishineachregionisreferredtointhediscussionbelow.

Thethreeoceanicregionsdifferedsignificantlyinaveragepopulationtrend(Figure8andAppendix2:TableofANOVAresults).Thisdifferenceseemstobelargelydrivenbyvariationinfishpopulationabundance—therewerenosignificantregionaldifferencesforbirdsormammals.Figure9showsthesignificantdifferencesinratesofpopulationchangeamongtheoceanregions(F=9.32,df=2,p=0.00),highlighting,atthepopulationlevel,thedecliningtrendintheAtlantic,smallaverageincreaseintheArctic,andlargestpositivechangeinthePacificOcean.ThepronouncedincreaseinthePacificOceanindexisnotasapparentwhenlookingatthemeanratesofchangeanditislikelythattheindexisbeing

drivenbyafewrapidlyincreasingmammalandfishspecies.This,andthecleardifferencesintrendsamongtheoceanbasins,particularlyfrom1975to1995,canbeexploredfurtherbylookingatpatternsintheBeringSeaandAleutianIslands(Box1).

TrendsintheAtlanticOcean,thesmallestdatasetofthethreeArcticregions,aredrivenpredominantlybyfishandbirds.Arcticclimate-drivenregimeshiftsarethoughttohaveoccurredintheNorthAtlantic(Greeneetal.2008)butduetobothnorthwardandsouthwardmovementofspeciesinresponsetothechangingconditions,teasingouthowthismighthaveaffectedoverallabundancetrendsisanalyticallycomplex.Onepossibilityisthatchangestoenvironmentalconditionsmayoperateintandemwithexploitationeffectstofacilitateapopulationdecline.Alternatively,theycouldimpedeanoverexploitedspecies’recovery,assuggestedforthecaseofAtlanticcod(Beaugrandet al.2008).IntheArcticOceanindex,theincreasefrom1987isdrivenbyfishandmammalspeciesasthebirdtrendsarelargelystableacrossthetimeseries(Appendix4:Tableofindexvalues).

The Arctic Ocean. Photo: George Burba/Shutterstock.com

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Figure8.Indicesofabundancebyoceanregion,1970to2005.IndicesareaveragedfortheArcticOcean(52species,113populations),AtlanticOcean(22species,44populations),andthePacificOcean(75species,153populations).

Figure9.Boxplotshowingthemedianannualrateofchangeoffishspeciesineachoceanicregionfrom1970to2005

Datasets–ArcticOcean:20populations;AtlanticOcean:16populations;PacificOcean:62populations.

Boxplotinterpretation:thehorizontallinesarethemedians;thetopsandbottomlinesoftheboxesrepresentthe75thand25thpercentilesrespectively;thetopandbottomend-pointstotheverticaldashedlinesrepresentthe95thand5thpercentilesrespectively.

Totallambdaisameasureoftherateofchangeovertheentiretimeperiod.

Sea otter. Photo: TTphoto/Shutterstock.com

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Themarineindexshowsanoverallincreaseinvertebrateabundancefrom1970to2005butthespatialdistributionofthepopulationtimeseriescontributingtotheindexisnotuniformacrosstheArcticmarineenvironment(Figure4).MuchofthecurrentmonitoringeffortappearstobelargelyclusteredaroundtheBeringSeaandAleutianIsland(BSAI)area.Thenumberofpopulationsfromthisregion(n=138),whichisasubsetofthePacificOceandataset,outweighsthenumberofpopulationsfromtheArcticOcean,AtlanticOcean,andtherestofthePacificOceanindividually,butnotcombined(n=172).

InordertoinvestigatetheextenttowhichpopulationsfromtheBSAIdrivetheoverallmarineindextrend,thepopulationsfromthisregionwereanalysedseparately.Theresults(Figure10)suggestthatabundancetrendsfromtheBSAIdoexertalargeinfluenceonthemarineindex,particularlyfrom1985to1995,butthatanincreaseinabundanceisstilloccurringintheremainingmarineregionscombined.

AcloserexaminationoftheBSAIregion(Figure11)revealsthatfishandmammaltrendsshowanoverallincrease,whereasbirdtrendsshowanoveralldecline.Anoverallcauseofthedecliningbirdtrendisnotevidentasthepresenceandnatureofthreatsvaryamongbirdspecies.Evenwithinspecies,identifyingprecisecausesofdeclineissometimescomplicatedbyspatialandtemporalfluctuationsoccurringsimultaneously(Byrdet al.2008).OneexampleofaspeciesfromthisregionindeclineisRissa brevirostris(Red-leggedkittiwake).Theeffectsofasubstantialfisheriesindustrymediatedthroughhabitat

disturbanceordisruptionofthefoodwebareapossiblecauseofdecline(Byrdet al.1997).EarlydeclinesofseabirdsintheAleutianislandsinthe20thcenturywerethoughttobeduetofoxpredation(Crollet al.2005)butitisunclearwhetherthiswouldbethemajordriveroftrendsafter1970.

Bering Sea effect

Figure10.IndicesofabundanceformarinepopulationsshowingtheeffectofremovingtheBeringSeaandAleutianIslandpopulations.BSAIdatasetscomprised71species,138populations.

Northern fur seal. Photo: VasikO/Shutterstock.com

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Themarinemammalincrease(Figure11)isnotconsistentacrosstheentiretimeperiod,withadefinitiveshiftindynamicstoadeclinein1988,whichcontinuesuntil2005.Thisisaresultofincreasingpopulationtrendsforsixcetaceanspeciesforwhichmonitoringendedin1989andhighlightstheimportanceofimplementinglong-termmonitoringtoavoidbreaksindatasetsthatcaninfluencetheindextosuchadegree.Ifthesesixcetaceanpopulationsareremovedfromthedataset,theindexshowsanoveralldeclineinabundanceof43%from1970to2005.Thisconstantdeclineintrendisreflectiveofthefollowingspecies:belugawhale,Stellersealion,harbourseal,seaotter,Pacificwalrus,northernfurseal,graywhale–forreasonsincludingincreasedpredation(Doroffet al.2003),lossofsummerseaice(Kovacset al.2010),anddepletedpreyresource(Mooreet al.2003),(Trites&Donnelly2003).

FishspeciesfromtheBSAI,onaverage,increasedinabundancefrom1970to1993(Figure11)andthistrenddrivestheoverallfishindexand,toacertainextent,themarineindex.Anotherbroadscalestudy(Hoff2005)alsofoundpositivechangesinbiomassintheeasternBeringSeashelfforallfishguildsinthe1970sand1980s.Thissuggeststhatfavourableenvironmentalconditionsarelikelytoberesponsiblefortheincreases.Thechangeintrendafter1993toadeclineandthentoastabletrendcouldbeduetolowproductivityobservedingroundfishintheeasternBeringSeaduringthe1990s(Mueter&Megrey2005).

Figure11.IndicesofabundanceformarinepopulationsfromtheBeringSeaandAleutianIslandregion(BSAI)forbirds,fishesandmammals

BSAIdatasets–birds:21species,54populations,fishes:37species,53populations,mammals:13species,31populations

Steller sea lions. Photo: Caleb Foster/Shutterstock.com

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Ecological trends

Sea ice association

RecentchangesinseaiceextentintheArctichavebeenwelldocumented(Stroeveet al.2007;Polyaketal.2010)andthereisevidenceemergingthatthisrapidshiftishaving,attimes,adverseeffectsonbiodiversity(Gleason&Rode2009;Heide-Jørgensenetal.2010;Kovacsetal.2010).Thenatureofaspecies’associationwithseaiceisimportantandvariesfromtheavailabilityoficealgaeasthebasisofthefoodwebstotheprovisionofsuitablehabitatforbreedingandforuseasahuntingplatform(Marz2010).

TheASTIdatasetcontainspopulationtrendsforninespeciesthathaveastrongassociationwithseaice(Arcticcod,ivorygull,thick-billedguillemot,bowheadwhale,belugawhale,narwhal,Pacificwalrus,ringedseal,polarbear).Thedatasetforseaiceassociatedspecieswasnotsufficienttoproduceanoveralltrendindexduetoalargevariationintimeserieslengthsforeachspecies,aswellasdiscontinuousperiodsofmonitoring.Lookingatthepopulationtrendsovertheentiretimeperiodforeachspecies,fourice-associatedspecies—ringedseal,belugawhale,Pacificwalrusandthick-billedguillemot—showedoveralldeclinesinabundance(alowerpopulationattheendofthemonitoringperiodthanatthebeginning).Thereweremixedtrendsamongthe36populations(Figure12)butjustoverhalfshowedanoveralldecline.Inlightofthepaucityofavailabledataandthewarningsignofanumberofnegativetrends,thereisclearlyanurgentneedtomonitorthesekeyArcticspecies.

Figure12:Knownstatusofindividualpopulationsfornineiceassociatedmarinespecies.

Forabreakdownbyspeciesandpopulations,seeAppendix5:Tableofpopulationtrendsfornineseaiceassociatedspecies.

Note:thestatusshownforPacificwalrusrepresentsthedecliningtrendinrecentdecades(1980to2006)whichfollowedaperiodofincrease–thetrendovertheentiretimeperiodofmonitoringwasanincrease.

Sea ice associated seal. Photo: Irina Igumnova/Shutterstock.com

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Regime shift

Environmentalchangesinthemarinesystemareprojectedtoleadtoashiftinspeciescompositionfrombenthictopelagic—thisisthoughttooccurinresponsetowarmerseasurfacetemperatures(Richter-Menge&J.Overland2010)andassociatedreductioninsummerseaiceextent.Weinvestigatedthisbyassigningeachspeciestothebenthic,pelagicorbenthopelagicmarinezone(seeAppendixTable1-Bfordefinitions).Lookingatthefishspeciesbrokendowninthisway(Figure13)providesnoevidenceofsuchashift.Bothbenthicandpelagicspeciesexhibitedanoverallincreaseinabundance,withthepelagicfishesshowingadistinctcyclicalpatternthroughoutthetimeseries.Thiscyclicalpatterncouldbeconcomitanttochangesoccurringinthemarineenvironmentinsimilarcycles.Thesixspeciesofbenthopelagicfishalsoincreasedinabundancefrom1970,butthisincreasecontinuedonlyuntilabout1998,whenalargelydecreasingtrendbeganandpersisteduntil2005.Withonlysevenspeciesofpelagicfishinthedataset,thetrendcouldbedrivenbyasmallnumberofthesespecies.Naturalresourcemanagementmayalsohaveaneffect,especiallyconsideringthatsomeofthesespeciesareofhighcommercialimportance(Box2).

Figure13.Indicesofabundanceforbenthic,pelagic,andbenthopelagicfishspeciesfrom1970to2005.

Datasetscomprised

• benthicfishes:42species,63populations;

• pelagicfishes:7species,14populations;

• benthopelagicfishes:6species,21populations.

Arctic ciso drying in the sun. Photo: Rumo/Shutterstock.com

Arctic char. Photo: Dan Bach Kristensen

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Pelagic fish trends

TobetterunderstandtheapparentcyclicpatterndeterminedforthepelagicfishasshowninFigure13,wecomparedtheoverallpelagicfishindextotheestablishedclimateoscillations(Pacific,Decadal,Arctic,andNorthAtlantic).FromthisanalysisthereappearedtobeastrongassociationbetweentheoverallpelagicfishindexwiththeArcticOscillationindexwithpeaksinthepelagicindexin1977,1983,1993,2002,and2009generallytrackingthepeaksintheArcticOscillation.Atthiswidespreadscale,therefore,theredoesappeartobealink(Figure14).

However,itisimportanttorelatethepatterntohabitatindicatorsthatauthorshaveidentifiedassignificantfactorsinthesurvivalandthusproductivityofpelagicspecies.Forexample,authors(NPFMC2008)notethatPacificherringrecruitmentintheTogiakherringpopulation(BristolBay,Alaska)ishighlyvariable,withlargeyearclassesoccurringatintervalsofbetweennineand10years.Further,thereisgoodevidencethatenvironmentalconditions—especiallyairandsea-surfacetemperature—relativetospawnruntimingareimportantfactorsindeterminingPacificherringrecruitmentintheBeringSea(Williams&Quinn2000).

PotentialdriversofherringpopulationchangewereexaminedinrelationtotheTogiakherringdataset(NPFMC2008).Theindicatorslookedatwere:sea-surfacetemperature(NOAA2011);summerbottomtemperature(Richter-Menge&J.Overland2010);meanannualtemperature(GeophysicalInstituteUniversityofAlaskaFairbanks2011);seaicecover(Richter-Menge&J.Overland2010).Thesewereallhighlyvariableanddidnotappeartopeakonanineto10yearcycleasissuggestedintheestimatedherringpopulationsize.Asanexample,seaiceextent(plottedonathreeyearrunningaverage)isshown(Figure15).Thiswastheclosestamongthevariablesto

Figure14.ComparisonofthethreeyearrunningaverageforthepelagicfishindexandtheArcticOscillation

Oscillationdatafrom:http://www.esrl.noaa.gov/psd/data/correlation/ao.data

Herring. Photo: fanfo/Shutterstock.com

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relatetoestimatesofpopulationabundanceofherringintheTogiakregionandillustratesthatthedriversbehindtheherringcyclesarenotabletobeexplainedbyasingleindicatorbutareinfluencedbyacomplexoffactors.

(Aydin&Mueter2007))provideacomprehensiveoverviewofthecomplexinteractionsthatmayberesponsiblefortheobservedcyclicalfishpopulationtrendsinthesoutheasternBeringSea.TheyreportthattheBeringSeahasexperiencedabruptshiftsinclimaticconditionssincethemid-1970swithassociatedfoodwebshifts.Theextentofseaiceandtimingoficeretreatiscriticalfortiming,overallbiomass,andfateofprimaryproduction—whichcomprisesmostlycopepods,animportantcomponentofpreyforvariousforagingfishspecies.Differencesinbloomtiminghavefavourableeffectsoneitherbenthicorpelagicspecies.Cyclesofdensity-dependentrecruitmentofvariousshorter-livedpelagicspecies,suchaspollockarealsolikelytointeractwiththecyclesinlonger-lived,competitorbenthicspeciessuchasflatfish.

Anotherfactornotincorporatedintheseabioticindicatorsishumanharvest.TheBeringSeaisoneofthemostproductivefisheriesintheworld(Walshet al.1989)anditsstockshaveexperiencedalonghistoryofexploitation,sothepossibleinfluenceoffishingpressureshouldalsobeconsidered.ThePacificherringpopulationdiscussedaboveisconsideredtobethreatenedbyexploitation(NPFMC2008).Whileoverfishingislikelytodirectlycauseadecreaseinabundanceofafishedspecies,thefishingpressureexertedonastockcouldalsohaveamorecomplexeffect.Fishingeffortandcatchintheregionarecloselymonitored,andadjustmentsaremadetoquota,basedonpastrecruitmentinthetargetspecies.Itispossiblethatthisadjustmentoffishingpressureinresponsetorecruitmentcouldinfluencecyclicalpatternsobserved(Williams&Quinn2000).Furthermore,humanpressurescanandwillinteractincomplexwayswiththeclimaticchangesobservedintheBeringSea.ThisanalysisisagoodexampleofhowaglobalscaleindexsuchasASTIcanrevealrelationshipswithkeydriversofspeciesabundancewhenthisisnotpossiblethroughfocussingonindividualpopulations.Thelatterapproach,however,isimportantinbetterunderstandingthemechanisms:howlarge-scaleoscillationsexertthemselvesonbiodiversityandabundanceandhowfactorsnotincorporatedintosimpleglobalindicesimpactlocalpopulations.

Figure15.ComparisonofestimatedherringpopulationsizeintheBristolBayareaandtheseaiceextentintheEastBeringSea

Bothplottedasthreeyearrunningaverages.HerringdatafromNPFMC(2008);seaicedatafromhttp://www.arctic.noaa.gov/reportcard

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Trophic level

Pursuingthethemeofecologicalinteractions,Figure16showstheaverageratesofchangebrokendownbythetrophiclevelofthespecies.Wemightexpecttoseedifferencesamongthetrophiclevelsinresponsetoenvironmentalfluctuationsandthecorrespondingchangesinforagingconditions.Forexample,impactsspecifictopiscivorousseabirdshavebeenexploredunderscenariosofachangingclimate(Stempniewiczet al.2007).Therefore,wedisaggregatedthedataforbirdsandfishesintofish-feedingandplankton-feedingspeciestoseeiftherewereanypatternsintheratesofchange.

Figure17comparestheresultingtrendsinfishandplanktonfeedingfishandbirds.Thereisnocleardifferenceintrendsamongthefishgroupsbutthebirdindicesdiffersignificantlyafter1985.Unlikethefish,thetrendsinpiscivorousbirdsareinconcordancewiththemediannegativerateofchangeforallsecondaryconsumersoffish(Figure16).Thebirdpopulationdeclinesinthisdatasetcouldbearesultofdetrimentalchangestoforagingconditionsasfoundinsomespeciesandlocations(Byrdet al.2008)oraresponsetoananthropogenicthreat.Thebirdpopulationsinquestionareaffectedbydifferentthreattypesandlevels,soitisnotpossibletomakeanyoverarchingconclusionsaboutthedeclineinpiscivorousseabirdsatthisstage.

Figure16.Boxplotshowingmedianrateofchangebytrophiclevelforparasitesandforprimary,secondary,andtertiaryconsumers

Datasets–parasites:4populations;primaryconsumers(Prim):2populations;secondaryconsumersoffish(Sec-fish):183populations;secondaryconsumersofinvertebrates(Sec-inv):68populations;secondaryconsumersofothervertebrates(Sec-vert):9populations;tertiaryconsumers(Tert):44populations.

Boxplotinterpretation:thehorizontallinesarethemedians;thetopsandbottomlinesoftheboxesrepresentthe75thand25thpercentilesrespectively;thetopandbottomend-pointstotheverticaldashedlinesrepresentthe95thand5thpercentilesrespectively.

Totallambdaisameasureoftherateofchangeovertheentiretimeperiod

Figure17.Trendsinabundanceindicesforspeciesofpiscivorousandplanktivorousbirdsandfishesfrom1970to2005

Datasets

• piscivorousbirds:22species,116populations;

• piscivorousfishes:26species,44populations;

• planktivorousbirds:4species,17populations;

• planktivorousfishes:15species,25populations.

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Theunderlyingtrendsfortertiaryconsumerscontrastwiththecommonthemethroughouttheseresultsofdeclinesinbirdpopulationsandincreasesinmammalsandfish(Appendix2:TableofANOVAresults).ThetwoeaglespeciesinthiscategoryshowanaverageincreasewhereasthepopulationsofOrcinus orca (killerwhale)andUrsus maritimus(polarbear)showanaveragedecline.ThefishdatasetisthelargestinthetertiaryconsumercategoryandisdominatedbyGadus morhua(Atlanticcod),Sebastes marinus(Oceanperch)andReinhardtius hippoglossoides(Greenlandhalibut)populationswhicharedrivingthemeanpopulationrateofchangeinthisgroup.Themajorityofpopulationsofthesespeciesarethreatenedbyexploitationsoitisnotsurprisingthattherateofchangefortertiaryfishandtheoverallaverageforthethreeclassesisnegative(Figure16).

Conservation management trends

Anthropogenic threats

Examininganthropogenicthreatstomarinepopulationscangiveanindicationofthepredominantpressuresaffectingspeciesabundance.Forthisanalysis,populationsthathadananthropogenicthreatidentifiedasbeingassociatedwiththembytheauthorsofthesourcedocumentwereconsideredtobeunderthreat.Optionsforthreatcategoryare:‘habitatloss’,‘habitatdegradation’,‘climatechange’,‘disease’,‘pollution’,‘exploitation’,and‘invasivespecies’.Notethat‘exploitation’,whichincludesaccidentalmortalityaswellasharvesting,isthereforeonlyassociatedwithapopulationifitisidentifiedasathreattothepopulationbythesourceauthor.Populationsthatweredescribedasnotcurrentlythreatenedwereplacedinthe‘nothreats’categoryandtheremainingoneswithnoinformationweretaggedas‘unknown’(seedatatagginginAppendix1:Methods).

Figure18showsthat,althoughencouraginglyboththreatenedandnon-threatenedpopulationsincreasedinabundanceoverthe35-yearperiod,thetrajectoriesofthetwoindicesaresubstantiallydifferent.Inaddition,thepopulationsunderthreatstabilisedinabundanceduringthemid-1980sandhavebeeninaslowdeclineeversince.Thepopulationsinthe‘unknown’categoryhaveseenlittlechangeinabundanceoverthistimebutappeartobefaringslightlyworsethanthethreatenedpopulations.Thishighlightstheneedtoobtainmoreinformationonthesedata-poorspeciesandlocations.

Figure18.Indicesofabundanceforpopulationsbythreatclassificationfrom1970to2005

Datasets

• populationsunderanyanthropogenicthreat:57species,110populations;

• populationsundernothreat:42species,57populations;

• thoseforwhichnoinformationisavailable:49species,143populations

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Forthosepopulationsthatareidentifiedasthreatened,‘climatechange’and‘exploitation’appeartobehavingthegreatesteffectonmedianrateofchange(Figure19).Theseresultsaresignificant;howevertheanalysisincludesdataforpopulationswherethreatinformationisnotknown.Whenthe‘unknown’andthe‘nothreat’categoriesareexcludedfromtheanalysisandthemedianratesofchangearecomparedbytaxonomicclass,thereareonlysignificantdifferencesbythreattypeforbirdpopulations(Appendix4:Tableofindexvalues).Anegativerateofchangeisobservedforpopulationsthreatenedby‘climatechange’and‘exploitation’,whichsuggeststhatbirdsaredrivingtheresultsforallclassesinFigure19.

Informationonthreatswascollatedfromthedatasourceswherethepopulationdatawaspublished.Becausethescopeandobjectivesofeachsourcedocumentvariedaccordingtothesubjecttheauthorsweretackling,thereissomedisparityintheamountofthreatinformationthatisavailableforeachpopulation.TomakebetteruseoftheASTIintrackingandunderstandingtheimpactsofthesethreatstoArcticbiodiversity,itisthereforeimportanttoimprovenotonlytheanimalpopulationdata,butalsothequality,comparability,andcoverageofdataonthreatstopopulations.Variablesthatcanbeusedtopredictchangesinpopulations,includingmeasuresofanthropogenicthreats,arediscussedfurtherinareportonspatialanalysisoftheASTIdataset(Bohmet al.2012).

Protected areas

Table3showsthenumberofpopulationsthatoccurwithinprotectedareas(‘yes’),entirelyoutsideprotectedareas(‘no’),andnotentirelywithinorwithoutprotectedareas(‘no–largesurveyarea’).Thetrendanalysiscomparingprotectedandunprotectedpopulationsshowedverysimilarlevelsofpopulationchange(Appendix4:Tableofindexvalues).Theprotectedpopulationsaremainlybirdspecieswhichwouldsuggestthatdataareprimarilyfromcoastallocations.Mostofthemarinemammalandfishpopulations,however,aresurveyedinsuchlargeareasthatnoneofthemareentirelyprotected.

Located within a protected area?

Populations

Mammals Birds Fishes

yes 21 95 4

no 7 30 12

no-largesurveyarea 27 21 82

total“no” 34 51 94

Figure19.Boxplotshowingthemedianratesofchangeofbirdpopulationsforwhichathreatisidentified,groupedbyprimarythreat,1970to2005.

Datasets–threatstobirdpopulations:climatechange(CC):12populations;disease:1population;exploitation(exploit):4populations;habitatdegradation(habdeg):7populations;invasivespecies(inv):1population;pollution:3populations.

Boxplotinterpretation:thehorizontallinesarethemedians;thetopsandbottomlinesoftheboxesrepresentthe75th

and25thpercentilesrespectively;thetopandbottomend-pointstotheverticaldashedlinesrepresentthe95thand5thpercentilesrespectively.

Totallambdaisameasureoftherateofchangeovertheentiretimeperiod.

Table3.Totalnumbersofpopulationsandspeciesthatarefoundinsideandoutsideprotectedareas

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Althoughtheoverallindicesofpopulationchangeforvertebrateswithinprotectedareasandvertebratesnotwithinprotectedareasaresimilar,ifwelookonlyatbirdpopulationsbirdpopulationsinprotectedareasarefaringfarbetterthantheircounterpartsinunprotectedareas(Figure20).BirdpopulationsinunprotectedareaswerefoundprimarilyalongthewestandnortheastcoastofIceland,theMurmanskandTaimyrregionsofRussia,andthenorthernpartofNorway,includinglocationsintheBarentsSea.Someoftheseregionshavealongtraditionofutilisingseabirdpopulations(Denlinger&Wohl2001),althoughthenumberofspeciesutilisedandamountofharvesttakenareoftenonlyafractionofformerlevels(Merkel2010).HuntingisstrictlyregulatedinNorwayandSvalbardandposesnoparticularthreat(Bakken&Anker-Nilssen2001).InRussia,Alcidscanbehuntedlocallyatparticulartimesoftheyear,withnohuntingallowedatseaintheBarentsSearegion(Golovkin2001).

Onepotentialcauseofdecline(especiallyinpastdecades)ofmarinebirdsnotinprotectedareasisthewidespreadutilisationofmarinebirdsthroughouttheArctic(Merkel&Barry2008).AroundtheArctic,themostcommonspeciesharvestedareCommonmurresandCommoneiders,andthecountrieswiththehighestharvestlevelsareIceland,Canada,andGreenland(Merkel2010).Thefollowingsectionconsiderstwomeasuresrecordedforeachpopulationtimeseriesinthedataset:1)isthepopulationknowntobeutilised(throughregularorsystematicharvesting,includingcollectionofeggs);and,2)isthepopulationthoughttobeimpactedbyexploitation(includingbothharvestingandaccidentalkilling,forexamplethoughentanglementinfishingnets).

TheharvestofseabirdsusedtobewidespreadinNorwayandSvalbardbutnowadaysstrictregulationsandyear-roundprotectionofmostspeciesresultinaverylowharvestrateofanaverageof5,000birdsperyear,thereforenotposingaparticularthreat(Merkel&Barry2008).Ofthe11Norwegian

Female and male common eiders. Photo: Micha Klootwijk/Shutterstock.com

Figure20.Indicesofabundanceforprotectedandunprotectedbirdpopulationsfrom1970to2005.

Dataset

• protected:30species,95populations;

• unprotected:17species,51populations.

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populations,onlytwoarethreatenedbyexploitation(Steller’seiderfromVarangerfjord,andCommonmurrefromFinnmark),butnotbeingatargetspeciesandwithnoindicationofbeingutilisedcouldpointtoapotentialimpactfromoutsidethecountry.InRussia,seabirdharvesthasneverbeenofprimaryimportancefortheeconomyorlocalcommunities,withtheexceptionofindigenouspeopleinhabitingthenorthandfareastofthecountry(Merkel&Barry2008).Noofficialfiguresontheharvesttakenannuallyexist,buttheyarebelievedtobelow,asmostoftheimportantbirdcoloniesarenowprotected(Merkel&Barry2008).Nevertheless,poachingcouldbealocalizedproblem,especiallyinremoteareas(Merkel&Barry2008).OftheRussianpopulationsinthedataset,nonearerecordedasbeingutilisedandonlySteller’seiderisconsideredtobethreatenedbyexploitation.However,asthisisacountry-wideestimate,over-harvestingisunlikelytobethesinglereasonfortheobserveddeclineinbirdsinunprotectedareas.

Onethirdofpopulationsinthedatasetareexplicitlynotutilised;weonlyhaveinformationconfirmingutilisationforonepopulation,whichisSomateria mollissima(commoneider)fromsouthwestIceland.Theutilisationstatusforotherpopulationsisunknown.Interestingly,threedifferentpopulationsofblackguillemotandnorthernfulmararelistedasbeingthreatenedbyexploitation,althoughthisisthroughbycatchandnotintentionalharvesting.

Overall,thereisnoevidencetosuggestthatunsustainableharvestcouldbethecauseofdecliningtrendsinseabirdpopulationsoutsideofprotectedareasintheArctic.Butasthemajorityofpopulationdatasetsarenotaccompaniedbyinformationonutilisationstatusoronexploitationasapotentialthreat(thesesourcesareinlanguagesotherthanEnglish),thisremainsapossibilityandcouldbefurtherexploredbyimprovingthedataonutilisationandexploitationandonfocussingtheanalysisonspeciesthataretargetedforharvestorarevulnerabletootherformsofexploitation.

Acknowledgements

Wewouldliketothankandacknowledgeallofthedatacontributorstothe2010ASTIreport(McRaeet al.2010).WewouldalsoliketothankJoRocheandHannahMacGregorforenteringnewdata,andTomBarryandMichaelSvobodaforreviewingthereportandfortheirhelpfulcommentsandsuggestions.FinallywewouldalsoliketoacknowledgeEnvironmentCanadaandtheCAFFSecretariatforprovidingfundsforthisreport.

Bird cliff. Photo: Maksimilian/Shutterstock.com

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Appendix 1: Methods

Population data

TimeseriestrendsforArcticspecieswerecollatedbyCAFF´sCBMPandfromtheLivingPlanetDatabase(Lohet al.2005;Collenet al.2009;www.livingplanetindex.org).Thesedatawerecollatedfrompublishedscientificliterature;onlinedatabases;Arcticresearchersandinstitutions;andfromgreyliterature.

FollowingCollenet al.(2009)datawereonlyincludedif:

• measureorproxymeasureofpopulationsize–e.g.,fullpopulationcount,biomass,catchperuniteffort,density(AppendixTable1-A)-wasavailableforatleast2years;

• informationwasavailableonhowthedatawerecollectedandwhattheunitsofmeasurementwere;

• thegeographiclocationofthepopulationwasprovidedandlaywithinthedefinedArcticboundaries;

• thedatawerecollectedusingthesamemethodonthesamepopulationthroughoutthetimeseries;and,

• thedatasourcewasreferencedandtraceable.

Data type Mammals Birds Fish Total

Biomass 68 68

Measureperuniteffort 1 9 10

Populationsestimateorcount 34 86 9 129

Other 25 66 12 103

Data tagging

Ancillaryinformationtothetimeseriesdatawasalsocollatedatboththespeciesandpopulationlevelencompassingdataongeographic,ecologicalandconservationmanagementthemes.ThosetagsusedtodisaggregatethemarinedataaredetailedinAppendixTable1-B.

Appendix Table 1- A.Datatypeofpopulationsbyclass

Northern fulmar Photo: David Thyberg/Shutterstock.com

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Data tag Details

System Terrestrial; Freshwater; Marine

Populationbased

Marineocean Atlantic;Pacific;Arctic

Primarythreat Informationontheprimaryanthropogenicthreattoapopulationwasrecordedifavailablefromthedatasource.Optionsforthreatcategoryarehabitatloss,habitatdegradation,climatechange,disease,pollution,exploitation,invasivespecies,nothreats,unknown

Protectedarea Yes;No(entirelyoutsideprotectedareas);No–largesurveyarea(populationwassurveyedinalargeareaandsonotentirelyinsideoroutsideaprotectedarea).TheWorldDatabaseonProtectedAreaswasusedtodiscernprotectedareastatus(IUCN&UNEP-WCMC2010)

Seaiceassociation Yes;No

Speciesbased

Trophiclevel Parasite;Primaryconsumer;Secondaryconsumer(fish);Secondaryconsumer(invertebrates);Secondaryconsumer(vertebrates);Tertiaryconsumer

Marinezone Benthic(livingandfeedingnearthebottomoftheocean);pelagic(livingandfeedingintheopensea);benthopelagic(livingandfeedingnearthebottomoftheoceanaswellasinmidwaterandnearthesurfaceorspecieswhichhoverorswimjustovertheseafloor–(Froese&Pauly2011))

Taxonomicclass Birds;mammals;fish(asthereareonlythreeElasmobranchspeciesinthedataset,wegroupedthesewithActinopterygiitocreateonefishclass)

Trend analysis

ForthemarineASTI,datawereaveragedatthespecieslevel(equalweightperspecies).ANOVAanalyses,however,wereconductedatthepopulationlevel.

AllanalyseswerecarriedoutinRversion2.12.0(RDevelopmentCoreTeam2006).IndicesofchangeinmarinespeciesabundancewerecalculatedusingaGeneralisedAdditiveModelling(GAM)frameworktoobtainpopulationtrendsandthenageometricaggregationmethodfollowingCollenet al.(2009)toproduceanindexofchange.Thedatasetwasdisaggregatedaccordingtothedatatagsabovetolookforunderlyingtrendsinthemarinedata.Inordertotestthesignificanceofseveralvariablesinassociationwithpopulationchange,wefirstcomputedthreemeasuresfromtherawpopulationtrendtimeseriesdata.Thesewere:

• slopeofalinearregressionofyearagainstpopulationsize(LRS);• meanannualchangeinpopulationsizecalculatedusingaGAMframework(MAC);and• totalchangeinpopulationsizeovertimeusingaGAMframework(TC).

Weobtainedthreechangemeasuresforeachpopulationandspeciesbygeneratingtheloggedtrendvaluesandmeanloggedtrendvaluesrespectivelyfromtheindividualpopulationtimeseriescalculatedbyeachofthemethodsabove.WecarriedoutANOVAstotrialeachofthethreemeasuresofpopulationchangeagainsteachofthediscontinuousvariablesandlinearregressionsofpopulationchangeagainsteachofthetwocontinuousvariables.Veryfewsignificantresultswereproducedatthespecieslevelsowehavereportedonlythosesignificantresultsatthepopulationlevel(seeAppendix2:TableofANOVAresults)andaswewereinterestedinthemostvariance,thetrendvalueweselectedtoreportonwasmeasuringtotalchange(TC),alsoreferredtoastotallambdaovertimeaswasusedonsimilaranalyses(Collenet al. 2011).Wedisplayedboxplotsforsignificantresultswhererelevant.

Appendix Table 1- B. Populationandspecies-baseddatatags

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Appendix 2: Table of ANOVA results

Factor Total lambda

df Sum sq Mean sq F value p value

Class 2 1.387 0.69344 1.5972 0.2041

Primarythreat(inclUnknown/No;allspp) 8 11.893 1.48661 3.6444 0.0004551***

Primarythreat(inclUnknown/No;birds) 8 6.415 0.8019 2.2363 0.02805*

Primarythreat(inclUnknown/No;fish) 4 5.321 1.33028 2.9809 0.02302*

Primarythreat(inclUnknown/No;mammals) 5 4.981 0.9962 2.2612 0.0612300000

Primarythreat(exclUnknown/No;allspp) 5 2.687 0.53738 1.4981 0.1968000000

Primarythreat(exclUnknown/No;birds) 5 4.1466 0.82931 4.3431 0.006696**

Primarythreat(exclUnknown/No;fish) 1 0.1133 0.11331 0.2265 0.6360000000

Primarythreat(exclUnknown/No;mammals) 2 0.1311 0.065545 0.3734 0.6927000000

Protectedlocation 3 2.276 0.75881 1.7538 0.1560

Protectedvsunprotected-allspp(YesandNoonly) 1 1.425 1.42516 3.1105 0.0796

Protectedvsunprotected-birds(YesandNoonly) 1 2.591 2.5911 6.9899 0.009265**

Protectedvsunprotected-fish(YesandNoonly) 1 0.046 0.04597 0.1007 0.7556

Protectedvsunprotected-mammals(YesandNoonly) 1 0.5361 0.53614 0.7003 0.4103

Protectedvsunprotected-allspp(Yes,No,Large=No) 1 0.621 0.62081 1.4107 0.2359

Protectedvsunprotected-birds(Yes,No,Large=No) 1 0.003627 0.003627 4.3371 0.03906*

Protectedvsunprotected-fish(Yes,No,Large=No) 1 0.511 0.51113 1.0595 0.3059

Protectedvsunprotected-mammals(Yes,No,Large=No) 1 0.5509 0.55085 1.1622 0.2859

Oceanbasin 2 7.126 3.5631 8.5762 0.0002375***

Ocean-birds 2 1.974 0.98697 2.6393 0.0748

Ocean-fish 2 7.682 3.8409 9.3222 0.0002011***

Ocean-mammals 2 0.0798 0.03992 0.0793 0.9239

BeringSeasplit(BeringvsRest;allspp) 1 1.376 1.3763 3.1801 0.0755

BeringSeasplit(BeringvsRest;birds) 1 0.086 0.08641 0.225 0.6360

BeringSeasplit(BeringvsRest;fish) 1 1.74 1.74006 3.7052 0.0572

BeringSeasplit(BeringvsRest;mammals) 1 0.0024 0.00238 0.0048 0.9450

Trophiclevel 5 5.285 1.05703 2.4835 0.03176*

Tertiaryconsumerbyclass 2 3.683 1.8415 5.0372 0.01106*

Sea-iceassociation 1 0 0.00005 0.000100 0.9919

Marinezone-benthic,pelagic,benthopelagic 2 2.129 1.06443 2.465400 0.0867

Marinezone-fish 2 3.125 1.56266 3.3972 0.03758*

Marinezone-birds 2 0.001112 0.000556 0.668100 0.5142

Protectedlocation(allspp) 3 2.276 0.75881 1.7538 0.1560

PAtype(all,inclunprotected) 3 1.111 0.37043 0.8487 0.4682

PAtype(yesandbothonly) 3 2.138 0.71253 1.8886 0.1348

Depthstratum 2 2.782 1.391 3.2378 0.04060*

Depthstratum(fish) 1 0.103 0.10285 0.2113 0.6468

Utilised(allspp) 2 0.304 0.15193 0.3471 0.71

Utilised(fish) 2 0.91 0.4551 0.9417 0.39

Highlightedcellsdenotesignificantresults*significantatp<0.05level**significantatp<0.01level***significantatp<0.001level

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aste

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chatka

Page 35: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

35Cl

ass

Bino

mia

lCo

mm

on n

ame(

s)Co

untr

yLo

cati

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f Pop

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chatka

Page 36: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

36Cl

ass

Bino

mia

lCo

mm

on n

ame(

s)Co

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yLo

cati

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f Pop

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ulpin

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Page 37: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

37Cl

ass

Bino

mia

lCo

mm

on n

ame(

s)Co

untr

yLo

cati

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f Pop

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Page 38: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

38Cl

ass

Bino

mia

lCo

mm

on n

ame(

s)Co

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yLo

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on o

f Pop

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ther

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ates

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ietIslan

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Page 39: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

39Cl

ass

Bino

mia

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edKitt

iwak

eUnite

dSt

ates

BuldirIsland

,Alask

a

Unite

dSt

ates

StG

eorg

eIsland

,Alask

a

Unite

dSt

ates

St.P

aulIslan

d,A

lask

a

Riss

a tr

idac

tyla

Blac

k-legg

edKitt

iwak

eUnite

dSt

ates

Agattu

Island

,Alask

a

RussianFe

deratio

nArk

hang

elsk

ayaBa

y,N

ovay

aZe

mya

Page 40: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

40Cl

ass

Bino

mia

lCo

mm

on n

ame(

s)Co

untr

yLo

cati

on o

f Pop

ulat

ion

Svalba

rdand

JanMay

enIs

land

sBe

arIs

land

Unite

dSt

ates

Bluff

,Alask

a

Unite

dSt

ates

BuldirIsland

,Alask

a

Unite

dSt

ates

Cape

Lisbu

rne,A

lask

a

Unite

dSt

ates

Cape

Peirce,A

lask

a

Unite

dSt

ates

ChiniakBa

y,A

lask

a

Unite

dSt

ates

Chow

ietIslan

d,A

lask

a

Icelan

dHafna

berg

,Sou

th-W

estIce

land

Unite

dSt

ates

HallIslan

d,A

lask

a

Nor

way

Hjelm

søy,M

åsøy

,Finnm

ark

Nor

way

Hor

nøy,Vardø

,Finnm

ark

RussianFe

deratio

nKh

arlov,M

urm

ancoa

st,N

orth

-Wes

tRus

sia

Unite

dSt

ates

KoniujiIslan

d,A

lask

a

Icelan

dKr

isuv

ikur

berg

(Kris

uvik),SW

Icelan

d

Cana

daPr

ince

Leo

poldIs

land

,Nun

avut

Unite

dSt

ates

PualeBa

y,A

lask

a

Nor

way

Røst,R

øst,Nor

dlan

d

Unite

dSt

ates

Roun

dIsland

,Alask

a

RussianFe

deratio

nRu

biniRoc

k,H

ooke

rIslan

d,Franz

Jose

fLan

d

Icelan

dSk

oruv

ik,N

EIcelan

d

Nor

way

Sør-Varan

ger,S

ør-V

aran

ger,F

innm

ark

Unite

dSt

ates

StG

eorg

eIsland

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a

Unite

dSt

ates

St.P

aulIslan

d,A

lask

a

Som

ater

ia m

ollis

sim

aCo

mm

onEider

RussianFe

deratio

nBe

ringIsland

coa

st

Icelan

dNor

durkot

,Rey

kjan

esba

er,s

outh

wes

tIce

land

Unite

dSt

ates

Yuko

n-Ku

skok

wim

delta

Gre

enland

Zack

erbe

rgda

len,N

orth

eastG

reen

land

Ster

cora

rius l

ongi

caud

usLo

ng-tailedJa

eger

Cana

daSo

uthe

rnPlain,S

irmilikNationa

lPar

k,Bylot

Island

,(Q

arlik

turv

ikValley/m

aingo

osene

stingco

lony

)

Gre

enland

TheKa

rupe

lvValleyPr

ojec

t,TraillO,K

ongOsc

arsFjor

d,

Nor

th-Eas

tGre

enland

Ster

cora

rius p

aras

iticu

sArctic

Jaeg

er,P

aras

iticJa

eger,

Arctic

Sku

aRu

ssianFe

deratio

nKh

arlovIsland

,Mur

man

skCoa

st

Page 41: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

41Cl

ass

Bino

mia

lCo

mm

on n

ame(

s)Co

untr

yLo

cati

on o

f Pop

ulat

ion

Nor

way

Slet

tnes

,Gam

vik,Finn

mar

k

Ster

na p

arad

isae

aArctic

tern

RussianFe

deratio

nOne

shsk

iBay

,White

Sea

,Rus

sia

Nor

way

Pasv

iknatur

rese

rvat,Sør

-Varan

ger,F

innm

ark

RussianFe

deratio

nSe

venIsland

s,Mur

man

skCoa

st,R

ussia

Gre

enland

The4island

sof

Gro

nneEjland

Unite

dSt

ates

Yuko

n-Ku

skok

wim

delta

Uria

aal

geCo

mm

onG

uille

mot

Icelan

dHafna

berg

,Sou

th-W

estIce

land

Ru

ssianFe

deratio

nKa

rlovIsland

,Mur

man

sk,R

ussia

Icelan

dKr

isuv

ikur

berg

(Kris

uvik),SW

Icelan

d

Icelan

dSk

oruv

ik,N

EIcelan

d

Nor

way

Sylte

fjord

,Finm

ark,N

orway

Sv

alba

rdand

JanMay

enIs

land

sBe

arIs

land

,Nor

way

Nor

way

Hjelm

søy,M

åsøy

,Finnm

ark

Nor

way

Hor

nnøy

,Vardø

,Finnm

ark

Nor

way

Sor-Fu

gloy

,Tro

ms,Nor

way

Nor

way

Vedø

y,Ved

øy,N

ordlan

d

Unite

dSt

ates

Bluff

,Alask

a

Unite

dSt

ates

Cape

Peirce,A

lask

a

Unite

dSt

ates

HallIslan

d,A

lask

a

Unite

dSt

ates

Roun

dIsland

,Alask

a

Unite

dSt

ates

StG

eorg

eIsland

,Prib

ilofs

Unite

dSt

ates

StPau

lIslan

d,Prib

ilofs

Unite

dSt

ates

St.L

awre

nceIsland

Uria

lom

via

Thick-bille

dGuille

mot

Cana

daCo

atsIsland

,Nun

avut

Icelan

dHafna

berg

,Sou

th-W

estIce

land

Icelan

dKr

isuv

ikur

berg

(Kris

uvik),SW

Icelan

d

Ca

nada

Prince

Leo

poldIs

land

,Nun

avut

Icelan

dSk

oruv

ik,N

EIcelan

d

Ru

ssianFe

deratio

nBe

zym

yann

ayaba

y

Nor

way

Hor

noya

Gre

enland

KapBr

ewster

Ru

ssianFe

deratio

nKh

arlovIsland

Page 42: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

42Cl

ass

Bino

mia

lCo

mm

on n

ame(

s)Co

untr

yLo

cati

on o

f Pop

ulat

ion

Sv

alba

rdand

JanMay

enIs

land

sSv

alba

rd

Unite

dSt

ates

BuldirIsland

Unite

dSt

ates

HallIslan

d,A

lask

a

Unite

dSt

ates

StG

eorg

eIsland

,Prib

ilofs

Unite

dSt

ates

StPau

lIslan

d,Prib

ilofs

Unite

dSt

ates

St.L

awre

nceIsland

Xem

a sa

bini

Sabine

'sGull

Unite

dSt

ates

Yuko

n-Ku

skok

wim

delta

Mam

mal

sBa

laen

a m

ystic

etus

Bowhe

adw

hale

Unite

dSt

ates

Wes

tern

Arctic

sto

ck,A

lask

a(aka

Ber

ing-

Chuk

chi-

Beau

fortsto

ck).

Bala

enop

tera

acu

toro

stra

taM

inke

wha

leNor

way

Bare

ntsh

avet

,Grø

nlan

dsha

vet,Nor

skeh

avet

og

Nor

dsjøen

Icelan

dIcelan

dicco

asta

lwater

s

Unite

dSt

ates

Pribilo

fIsa

lnds

,Ber

ingSe

a

Bala

enop

tera

bor

ealis

Seiw

hale

Icelan

dIcelan

dicco

asta

lwater

s

Bala

enop

tera

mus

culu

sBlue

wha

leIcelan

dIcelan

dicco

asta

lwater

s

Bala

enop

tera

phy

salu

sFinwha

leGre

enland

Gre

enland

Icelan

dIcelan

d

Icelan

dIcelan

dicco

asta

lwater

s

Cana

daNew

foun

dlan

d

Unite

dSt

ates

Pribilo

fIslan

ds,B

eringSe

a

Callo

rhin

us u

rsin

usNor

ther

nfu

rsea

lUnite

dSt

ates

St.G

eorg

eIsland

(inth

ePr

ibilo

fIslan

dspar

toft

he

Aleut

ianIsland

s),A

lask

a

Unite

dSt

ates

St.P

aulIslan

d(in

thePr

ibilo

fIslan

dspar

toft

he

Aleut

ianIsland

s),A

lask

a

Del

phin

apte

rus l

euca

sBe

luga

Unite

dSt

ates

Cook

Inlets

tock

,Alask

a

Ca

nada

Easter

nHud

sonBa

ypo

pulatio

n

Unite

dSt

ates

Easter

nCh

ukch

iSea

Sto

ck,A

lask

a

Unite

dSt

ates

Nor

tonSo

und,A

lask

a

Enhy

dra

lutr

isSe

aot

ter

Unite

dSt

ates

Adak

Island

,Aleut

ianIsland

s,Alask

a

RussianFe

deratio

nBe

ringIsland

,Rus

sia

Unite

dSt

ates

Delarof

Island

s,Aleut

ianIsland

s,Alask

a.

Unite

dSt

ates

FoxIsland

,Aleut

ianIsland

s,Alask

a

Unite

dSt

ates

Nea

rIslan

ds,A

leut

ianIsland

s,Alask

a.

Page 43: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

43Cl

ass

Bino

mia

lCo

mm

on n

ame(

s)Co

untr

yLo

cati

on o

f Pop

ulat

ion

Unite

dSt

ates

Nor

thA

lask

anpen

insu

la,n

orth

east(o

ffsho

re)

Unite

dSt

ates

Nor

thA

lask

anpen

insu

la,s

outh

wes

t(off

shor

e)

Unite

dSt

ates

RatIslan

ds,A

leut

ianIsland

s,Alask

a.

Unite

dSt

ates

Sout

hAlask

ape

nins

ula,coa

stlin

eof

22island

s.

Unite

dSt

ates

Sout

hAlask

ape

nins

ula,False

Pas

sto

Cap

eDou

glas

,co

asta

l

Unite

dSt

ates

Sout

hAlask

anPen

insu

lafr

om(o

ffsho

re)fro

mth

eIkatan

Pen

insu

lato

Shu

mag

inIs

land

s

Esch

richt

ius r

obus

tus

Graywha

leUnite

dSt

ates

Nor

ther

nBe

ringSe

ainclud

ingSt

Law

renc

eIsland

Unite

dSt

ates

Pribilo

fIslan

ds,B

eringSe

a

Eum

etop

ias j

ubat

usSt

ellers

ealion

Unite

dSt

ates

Alask

a-W

este

rnsto

ck

Unite

dSt

ates

Cent

ralA

leut

ianIsland

s

Unite

dSt

ates

Easter

nAleut

ianIsland

s

RussianFe

deratio

nKu

rilIs

land

s

Unite

dSt

ates

Wes

tern

Aleut

ianIsland

s

Glo

bice

phal

a m

elas

Long

finn

edpilo

twha

leIcelan

dIcelan

dicco

asta

lwater

s

Hyp

eroo

don

ampu

llatu

sNor

ther

nbo

ttleno

sew

hale

Icelan

dIcelan

dicco

asta

lwater

s

Meg

apte

ra n

ovae

angl

iae

Hum

pbac

kwha

leIcelan

dIcelan

dicco

asta

lwater

s

Unite

dSt

ates

Pribilo

fIslan

ds,B

eringSe

a

Mon

odon

mon

ocer

osNar

wha

lCa

nada

Hud

sonBa

y,Can

ada

Odo

benu

s ros

mar

usPa

cific

walru

sUnite

dSt

ates

Berin

gan

dCh

ukch

isea

sof

Alask

aan

dRu

ssia

Orc

inus

orc

aKille

rwha

leIcelan

dIcelan

dicco

asta

lwater

s

Unite

dSt

ates

Pribilo

fIslan

ds,B

eringSe

a

Phoc

a vi

tulin

aHar

bour

Sea

lUnite

dSt

ates

Otter

Island

,Ber

ingSe

a,A

lask

a

Unite

dSt

ates

Nan

vakIsland

,Alask

a

Sw

eden

Nor

ther

nSw

eden

Unite

dSt

ates

Tugida

kIsland

,Alask

a

Phoc

oena

pho

coen

aHar

bour

por

poise

Icelan

dIcelan

dicco

asta

lwater

s

Phoc

oeno

ides

dal

liDall's

por

poise

Unite

dSt

ates

Pribilo

fIslan

ds,B

eringSe

a

Phys

eter

cato

don

Sper

mw

hale

Icelan

dIcelan

dicco

asta

lwater

s

Pusa

his

pida

Ring

edsea

lCa

nada

easter

nBe

aufo

rtSea

Urs

us m

ariti

mus

Polarb

ear

Unite

dSt

ates

Alask

anSto

ck

Page 44: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

44

Clas

sBi

nom

ial

Com

mon

nam

e(s)

Coun

try

Loca

tion

of P

opul

atio

n

Cana

daBa

ffinBa

y

Unite

dSt

ates

Chuk

chi/B

eringSe

astoc

k

Cana

daDav

isStrait

Cana

daNor

ther

nBe

aufo

rtSea

pop

ulation

Unite

dSt

ates

Sout

hern

Bea

ufor

tpop

ulation

Cana

daSo

uthe

rnH

udso

nBa

ypo

pulatio

n

Cana

daW

este

rnH

udso

nBa

ypo

pulatio

n

RussianFe

deratio

nW

rang

elIs

land

State

Natur

eRe

serv

e

Page 45: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

45

App

endi

x 4:

Tab

le o

f ind

ex v

alue

s

Theta

blepr

esen

tsfive

yea

rlyin

dexva

lues

and

num

bero

fpop

ulations

fore

achArctic

inde

xsh

owninth

ere

port.

1970

1975

1980

1985

1990

1995

2000

2005

AST

I 201

11

1.00

9841

1.07

8684

1.15

0389

1.23

9031

1.21

8304

1.16

5219

1.21

232

Lower

con

fiden

cein

terv

al1

0.94

8302

0.99

796

1.04

626

1.10

4754

1.07

5185

1.01

7745

1.04

8901

Upp

ercon

fiden

cein

terv

al1

1.07

6369

1.16

7175

1.26

6994

1.39

765

1.38

5632

1.33

4767

1.40

2085

Num

bero

fpop

ulations

224

283

353

411

469

571

619

503

Mar

ine

Mar

inesp

ecies

11.11

4247

1.31

7582

1.57

2679

1.88

2688

1.96

8758

1.89

5275

1.93

523

Lower

con

fiden

cein

terv

al1

0.96

5039

1.11

3791

1.28

8609

1.47

4931

1.52

5575

1.45

3415

1.46

4981

Upp

ercon

fiden

cein

terv

al1

1.30

8125

1.58

9431

1.93

303

2.41

3804

2.54

9569

2.47

1473

2.55

6968

Num

bero

fpop

ulations

6899

145

195

216

231

222

165

Mar

inebird

s1

0.99

7764

1.12

2378

1.28

987

1.31

4885

1.33

1219

1.23

6808

1.21

1394

Lower

con

fiden

cein

terv

al1

0.91

827

1.00

5529

1.12

5928

1.08

6834

1.06

1118

0.98

2468

0.86

91

Upp

ercon

fiden

cein

terv

al1

1.09

5847

1.24

4867

1.45

0622

1.59

9749

1.64

3055

1.59

3717

1.56

662

Num

bero

fpop

ulations

3449

7410

311

512

411

592

Mar

inem

amm

als

11.20

2454

1.72

2755

1.82

7424

1.96

272.53

3504

2.47

6332

2.21

4405

Lower

con

fiden

cein

terv

al1

1.02

7889

1.17

436

1.23

7401

1.05

0436

1.27

0725

1.28

0015

1.05

5701

Upp

ercon

fiden

cein

terv

al1

1.38

9616

2.35

3404

2.64

3598

3.84

6035

4.65

1949

4.26

7893

3.83

6428

Num

bero

fpop

ulations

1020

2534

4146

4310

Mar

inefis

hes

11.21

5079

1.33

1957

1.77

474

2.57

9227

2.47

9329

2.42

4314

2.60

0284

Lower

con

fiden

cein

terv

al1

0.94

6687

1.01

7399

1.28

4341

1.70

1527

1.64

0312

1.62

3004

1.75

3774

Upp

ercon

fiden

cein

terv

al1

1.94

6065

2.07

7843

3.02

0004

4.34

7044

4.33

2616

4.05

346

4.44

3767

Num

bero

fpop

ulations

2430

4658

6061

6463

Taxo

nom

ic e

ffec

t

Mar

ine

11.11

4247

1.31

7582

1.57

2679

1.88

2688

1.96

8758

1.89

5275

1.93

523

Lower

con

fiden

cein

terv

al1

0.96

5039

1.11

3791

1.28

8609

1.47

4931

1.52

5575

1.45

3415

1.46

4981

Upp

ercon

fiden

cein

terv

al1

1.30

8125

1.58

9431

1.93

303

2.41

3804

2.54

9569

2.47

1473

2.55

6968

Num

bero

fpop

ulations

6899

145

195

216

231

222

165

Page 46: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

46

1970

1975

1980

1985

1990

1995

2000

2005

Minus

bird

s1

1.21

8977

1.50

363

1.84

363

2.41

092.56

1966

2.50

812.61

6509

Lower

con

fiden

cein

terv

al1

0.95

2601

1.11

7566

1.32

8514

1.64

1212

1.71

7797

1.66

3814

1.71

0984

Upp

ercon

fiden

cein

terv

al1

1.61

4112

2.08

8935

2.62

9027

3.64

9082

3.90

1905

3.83

919

4.05

9243

Num

bero

fpop

ulations

3450

7192

101

107

107

73

Minus

fish

es1

1.04

1276

1.27

3508

1.42

1223

1.46

926

1.63

6768

1.55

0269

1.49

6136

Lower

con

fiden

cein

terv

al1

0.95

9672

1.11

1677

1.20

1662

1.15

2716

1.26

1503

1.17

6684

1.10

393

Upp

ercon

fiden

cein

terv

al1

1.13

158

1.48

1346

1.72

0099

1.90

8795

2.15

271

2.05

8076

2.04

3897

Num

bero

fpop

ulations

4469

9913

715

617

015

810

2

Minus

mam

mals

11.09

9438

1.22

3274

1.50

9501

1.87

1507

1.84

258

1.76

6273

1.82

7372

Lower

con

fiden

cein

terv

al1

0.93

5411

1.02

1167

1.22

3764

1.45

7115

1.41

5932

1.34

2493

1.35

1402

Upp

ercon

fiden

cein

terv

al1

1.32

1133

1.49

2295

1.90

2881

2.43

3802

2.42

5199

2.35

1492

2.42

3714

Num

bero

fpop

ulations

5879

120

161

175

185

179

155

Oce

an b

asin

Arctic

Oce

an1

1.07

794

1.11

8803

1.03

1441

1.19

854

1.35

7803

1.42

4298

1.54

2828

Lower

con

fiden

cein

terv

al1

0.97

856

0.96

7883

0.83

3491

0.76

1469

0.87

7838

0.93

3275

0.94

5517

Upp

ercon

fiden

cein

terv

al1

1.17

7113

1.28

991

1.22

7842

1.62

1245

1.88

7448

1.91

7453

2.19

7517

Num

bero

fpop

ulations

3239

5064

8376

7147

Atla

nticO

cean

11.09

2007

0.97

1313

0.90

5974

0.79

2417

0.68

2281

0.69

8429

0.69

0356

Lower

con

fiden

cein

terv

al1

0.69

8235

0.60

3564

0.57

5761

0.49

9334

0.40

574

0.41

927

0.41

9878

Upp

ercon

fiden

cein

terv

al1

1.56

8681

1.42

2385

1.31

1167

1.15

544

0.99

4336

1.03

2576

0.97

9962

Num

bero

fpop

ulations

1922

3041

4036

2423

Pacific

Oce

an1

0.97

1865

1.33

2155

1.87

0811

2.36

7528

2.38

9436

2.14

8445

2.11

3518

Lower

con

fiden

cein

terv

al1

0.79

9362

1.04

0441

1.42

6487

1.72

7317

1.73

0009

1.53

118

1.51

2989

Upp

ercon

fiden

cein

terv

al1

1.22

5136

1.79

3921

2.58

2133

3.39

8477

3.49

1577

3.35

6503

3.16

0392

Num

bero

fpop

ulations

1738

6590

9311

912

795

Beri

ng S

ea

Berin

gSe

a1

1.04

2088

1.48

759

1.96

7571

2.48

797

2.47

797

2.24

5908

2.23

5218

Lower

con

fiden

cein

terv

al1

0.82

4813

1.13

8795

1.44

5061

1.83

258

1.86

2725

1.62

9392

1.58

9221

Upp

ercon

fiden

cein

terv

al1

1.22

0889

2.04

5222

2.66

7079

3.40

3583

3.34

0541

3.17

2907

3.33

482

Num

bero

fpop

ulations

1233

5584

8710

811

690

Page 47: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

47

1970

1975

1980

1985

1990

1995

2000

2005

Mar

inem

inus

Ber

ingSe

a1

1.17

1356

1.18

3236

1.20

6308

1.34

7492

1.46

2441

1.52

6446

1.62

6274

Lower

con

fiden

cein

terv

al1

0.98

1972

0.96

9959

0.90

0716

0.94

351

1.00

6895

1.07

1785

1.18

3513

Upp

ercon

fiden

cein

terv

al1

1.44

3303

1.50

594

1.53

7158

1.94

7833

2.11

1479

2.17

8463

2.46

748

Num

bero

fpop

ulations

5666

9011

112

912

310

675

Berin

gbird

s1

0.71

6961

0.75

6647

0.79

5857

0.97

2427

0.96

1084

0.84

8746

0.83

9834

Lower

con

fiden

cein

terv

al1

0.62

3031

0.65

2309

0.68

0874

0.74

8608

0.73

3071

0.62

605

0.57

0575

Upp

ercon

fiden

cein

terv

al1

0.82

0872

0.87

1604

0.92

5849

1.26

0082

1.25

8951

1.15

9308

1.21

743

Num

bero

fpop

ulations

110

2134

3749

5437

Berin

gfis

hes

11.16

6061

1.93

7049

2.99

9204

3.71

9842

3.88

4403

3.57

3027

3.69

2198

Lower

con

fiden

cein

terv

al1

0.76

1074

1.21

6892

1.78

5645

2.19

5324

2.24

9615

2.02

8019

2.05

3039

Upp

ercon

fiden

cein

terv

al1

1.77

3337

3.08

2026

5.01

3473

6.34

9981

6.65

3324

6.30

5691

6.65

5616

Num

bero

fpop

ulations

58

1830

3035

4148

Berin

gm

amm

als

11.15

8352

1.78

1006

2.25

3052

3.04

9295

2.54

1555

2.26

7056

1.81

0252

Lower

con

fiden

cein

terv

al1

1.06

2601

1.27

7659

1.48

4669

1.62

4318

1.29

5382

1.14

5237

0.90

6043

Upp

ercon

fiden

cein

terv

al1

1.24

7532

2.57

333

3.46

961

5.74

6624

5.07

4001

4.57

4479

3.68

8465

Num

bero

fpop

ulations

615

1620

2024

215

Sea

ice

asso

ciat

ion

Not

assoc

iate

d1

1.08

0857

1.29

4591

1.61

341.93

5442

1.97

9779

1.89

2574

1.94

0091

Lower

con

fiden

cein

terv

al1

0.88

611

1.09

9004

1.29

5827

1.46

4921

1.43

6947

1.44

2808

1.48

0081

Upp

ercon

fiden

cein

terv

al1

1.26

6706

1.56

9791

2.06

2277

2.46

2768

2.61

3275

2.49

8851

2.63

102

Num

bero

fpop

ulations

6492

132

171

191

205

198

148

Seaiceas

sociated

11.43

8163

1.47

8786

1.21

5271

1.38

2608

1.82

3801

1.90

005

1.84

7834

Lower

con

fiden

cein

terv

al1

1.21

3439

1.24

378

0.84

8826

0.89

7862

0.99

0532

0.96

9511

0.97

8472

Upp

ercon

fiden

cein

terv

al1

1.69

1054

1.75

5737

1.69

4164

2.08

8947

3.27

1395

3.28

2895

3.40

3608

Num

bero

fpop

ulations

47

1324

2526

2417

Mar

ine

zone

Bent

hicfis

h1

0.84

7484

1.01

5729

1.45

1804

1.96

7326

2.13

6922

2.06

0795

2.35

9461

Lower

con

fiden

cein

terv

al1

0.68

0872

0.78

0571

1.04

1065

1.32

2604

1.41

0522

1.34

0051

1.50

5985

Upp

ercon

fiden

cein

terv

al1

1.03

4374

1.30

791

2.00

8178

2.97

9518

3.26

9703

3.20

2652

3.71

8174

Num

bero

fpop

ulations

1013

2232

3441

4647

Page 48: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

48

1970

1975

1980

1985

1990

1995

2000

2005

Bent

hope

lagicfis

h1

1.34

8473

1.65

1483

1.78

4157

2.39

8219

1.36

1894

1.37

5197

1.15

7641

Lower

con

fiden

cein

terv

al1

0.68

7768

0.78

0432

0.74

494

0.89

4199

0.48

8127

0.43

6445

0.34

8927

Upp

ercon

fiden

cein

terv

al1

2.83

3867

3.62

7184

4.59

0298

6.67

3504

3.99

5494

4.58

0171

4.05

2748

Num

bero

fpop

ulations

910

1316

1613

1111

Pelagicfis

h1

2.11

1073

1.59

7818

1.53

8582

3.26

7538

2.60

4642

2.73

313

2.37

8078

Lower

con

fiden

cein

terv

al1

0.81

8447

0.56

5143

0.46

1006

0.70

1132

0.54

6403

0.52

764

0.45

5817

Upp

ercon

fiden

cein

terv

al1

5.90

7668

4.84

943

5.62

7016

17.883

314

.593

5416

.293

6114

.549

02

Num

bero

fpop

ulations

57

1110

107

75

Plan

ktiv

orou

s fe

eder

s

Pisc

ivor

ousse

abird

s1

0.97

3779

1.06

8846

1.08

3051

0.90

3676

0.90

3919

0.82

6194

0.74

2729

Lower

con

fiden

cein

terv

al1

0.86

7834

0.94

5021

0.95

4432

0.74

6605

0.73

5827

0.62

4446

0.51

7759

Upp

ercon

fiden

cein

terv

al1

1.06

8693

1.17

199

1.20

7084

1.01

5262

1.06

6673

0.99

4613

1.00

9821

Num

bero

fpop

ulations

2842

6182

9191

8366

Pisc

ivor

ousfis

hes

11.34

8937

1.20

5521

1.90

8059

3.46

1609

3.64

4552

3.57

3729

4.16

1422

Lower

con

fiden

cein

terv

al1

0.92

8582

0.71

0118

0.96

6247

1.85

0307

2.04

2281

1.99

8049

2.25

6241

Upp

ercon

fiden

cein

terv

al1

2.15

2773

2.08

003

3.27

0981

6.79

9244

7.22

117

7.08

5897

7.72

6046

Num

bero

fpop

ulations

99

1526

2931

3129

Plan

ktivor

ousse

abird

s1

0.80

3552

0.87

4373

0.98

3917

1.72

2304

1.64

1129

1.62

533

1.94

3556

Lower

con

fiden

cein

terv

al1

0.80

3552

0.75

156

0.83

6844

1.44

5102

1.33

1621

1.40

3463

1.54

2119

Upp

ercon

fiden

cein

terv

al1

0.80

3552

0.95

5237

1.30

4581

2.41

8211

2.33

0629

2.49

7926

3.87

7701

Num

bero

fpop

ulations

01

613

1418

1716

Plan

ktivor

ousfis

hes

11.49

9526

2.09

6872

2.57

4555

3.09

4991

3.16

1776

3.21

2127

2.97

1525

Lower

con

fiden

cein

terv

al1

0.78

4903

1.10

5678

1.26

009

1.43

6703

1.44

644

1.53

5758

1.36

0954

Upp

ercon

fiden

cein

terv

al1

2.99

681

4.61

6229

5.29

6864

5.89

4302

5.86

2755

6.87

1211

6.15

2875

Num

bero

fpop

ulations

611

1614

1415

1715

Thre

ats

Unk

nown

11.01

4925

1.07

8858

0.98

7633

1.05

0691

1.08

9163

1.11

2435

1.02

7479

Lower

con

fiden

cein

terv

al1

0.91

8452

0.96

2793

0.83

9148

0.75

0054

0.74

7863

0.75

0306

0.65

9168

Upp

ercon

fiden

cein

terv

al1

1.12

3089

1.21

3615

1.14

8177

1.49

2938

1.60

4574

1.66

9382

1.61

2894

Num

bero

fpop

ulations

3146

7190

115

116

105

66

Page 49: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

49

1970

1975

1980

1985

1990

1995

2000

2005

Noth

reats

11.01

1811

1.45

1504

1.99

6786

3.20

8091

3.75

7376

3.59

1975

4.08

0581

Lower

con

fiden

cein

terv

al1

0.70

798

0.90

1846

1.17

4586

1.79

7852

2.07

3388

1.96

1934

2.17

1151

Upp

ercon

fiden

cein

terv

al1

1.39

634

2.30

7871

3.36

0468

5.65

6222

6.64

2041

6.46

3931

7.56

2862

Num

bero

fpop

ulations

717

1932

2635

3939

Any

thre

at1

1.16

2646

1.22

5217

1.44

617

1.53

271

1.39

0152

1.39

6481

1.37

2785

Lower

con

fiden

cein

terv

al1

0.92

5443

0.94

7447

1.05

8939

1.09

8914

0.98

1926

0.97

4464

0.93

8049

Upp

ercon

fiden

cein

terv

al1

1.50

7447

1.63

3341

2.02

6676

2.18

7835

2.00

7798

2.04

2104

2.04

1828

Num

bero

fpop

ulations

3036

5573

7580

7860

Prot

ecte

d ar

eas

Prot

ecte

dbird

s1

0.97

5835

1.09

1298

1.26

9578

1.33

1779

1.36

3661

1.28

2401

1.21

469

Lower

con

fiden

cein

terv

al1

0.78

3012

0.86

3271

0.95

9008

0.97

2525

0.96

3008

0.89

1771

0.79

8613

Upp

ercon

fiden

cein

terv

al1

1.17

6186

1.34

6428

1.66

6638

1.81

4192

1.90

2935

1.83

6861

1.83

2926

Num

bero

fpop

ulations

1728

4967

7278

7659

Unp

rote

cted

bird

s1

0.88

1982

1.03

2164

1.10

4786

1.07

4551

1.05

1463

0.99

8881

0.97

4174

Lower

con

fiden

cein

terv

al1

0.79

6747

0.89

1092

0.93

0566

0.88

6453

0.84

260.78

9202

0.69

9173

Upp

ercon

fiden

cein

terv

al1

0.96

6151

1.20

4806

1.32

7638

1.31

2931

1.31

921.26

3694

1.45

2495

Num

bero

fpop

ulations

1519

2131

3941

3530

Page 50: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

50A

ppen

dix

5: T

able

of p

opul

atio

n tr

ends

for n

ine

sea-

ice

asso

ciat

ed s

peci

es

Tren

dsare

bas

edonth

eov

erallc

hang

einpop

ulationsize

.

Spec

ies

Com

mon

nam

eLo

cati

on o

f mon

itor

ed p

opul

atio

nRe

fere

nce

Popu

lati

on tr

end

Bala

ena

mys

ticet

usBo

whe

adw

hale

Wes

tern

Arctic

sto

ck,A

lask

a(a.k.a.B

ering-

Chuk

chi-

Beau

fortsto

ck).

(Ang

liss&O

utlaw200

6)St

able/Po

sitiv

e

Bore

ogad

us sa

ida

Arctic

cod

Bare

ntsh

avet

(Micha

lsen

200

4;Stia

nsen

&Filin20

08)

Stab

le/Po

sitiv

e

Sa

gava

nirkto

kDelta

,Alask

a(G

riffith

set

al.19

98)

Stab

le/Po

sitiv

e

Del

phin

apte

rus l

euca

sBe

luga

wha

leCo

okIn

lets

tock

,Alask

a(M

MC20

02;A

nglis

s&O

utlaw200

8;A

llen&A

nglis

s20

10)

Neg

ative

Easter

nCh

ukch

iSea

Sto

ck,A

lask

a(N

OAAFishe

ries:O

ffice

ofP

rote

cted

Res

ources

199

9)Neg

ative

Easter

nHud

sonBa

ypo

pulatio

n(D

FO200

5)Neg

ative

Nor

tonSo

und,A

lask

a(D

eMas

tere

t al.20

01)

Stab

le/Po

sitiv

e

Mon

odon

mon

ocer

osNar

wha

lHud

sonBa

y,Can

ada

(COSE

WIC

200

4)St

able/Po

sitiv

e

Odo

benu

s ros

mar

usPa

cific

walru

sBe

ringan

dCh

ukch

iSea

sof

Alask

aan

dRu

ssia

(Gar

ner1

995;N

OAA201

0a)

Neg

ative

Pago

phila

ebu

rnea

Ivor

ygu

llFran

z-Jo

sefL

and

(Ank

er-N

ilsse

net

al.20

00)

Stab

le/Po

sitiv

e

Vario

usin

Can

ada,G

reen

land

,Rus

sia,N

orway

(m

idpo

intlatitu

debelow

)(C

AFF

200

8)Neg

ative

Pusa

his

pida

Ring

edsea

lEa

ster

nBe

aufo

rtSea

(Stir

ling20

02)

Neg

ative

Uria

lom

via

Thick-bille

dgu

illem

otBe

zym

yann

ayaba

y(K

rasn

ove

t al.19

95)

Stab

le/Po

sitiv

e

Hor

noya

(Ank

er-N

ilsse

net

al.20

00)

Stab

le/Po

sitiv

e

KapBr

ewster

(Falk&Kam

pp199

7)Neg

ative

Khar

lovIsland

(Krasn

ove

t al.19

95)

Stab

le/Po

sitiv

e

Svalba

rd(A

nker

-Nils

sen

et a

l.20

00)

Stab

le/Po

sitiv

e

BuldirIsland

(Drago

oet

al.20

00;D

rago

oet

al.20

08)

Stab

le/Po

sitiv

e

StG

eorg

eIsland

,Prib

ilofs

(Drago

oet

al.20

00;D

rago

oet

al.20

08)

Neg

ative

StPau

lIslan

d,Prib

ilofs

(Drago

oet

al.20

00;D

rago

oet

al.20

08)

Neg

ative

Hafna

berg

,Sou

th-W

estIce

land

(Garoa

rsso

n&Zoc

ker2

006)

Neg

ative

Krisuv

ikur

berg

(Kris

uvik),SW

Icelan

d(G

aroa

rsso

n&Zoc

ker2

006)

Neg

ative

Skor

uvik,N

EIcelan

d(G

aroa

rsso

n&Zoc

ker2

006)

Neg

ative

CoatsIsland

,Nun

avut

(Gas

ton

et a

l.20

08b)

Stab

le/Po

sitiv

e

Prince

Leo

poldIs

land

,Nun

avut

(Gas

ton

et a

l.20

08b)

Stab

le/Po

sitiv

e

Page 51: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

51

Spec

ies

Com

mon

nam

eLo

cati

on o

f mon

itor

ed p

opul

atio

nRe

fere

nce

Popu

lati

on tr

end

HallIslan

d,A

lask

a(D

rago

oet

al.20

08)

Neg

ative

St.L

awre

nceIsland

(Drago

oet

al.20

08)

Neg

ative

Urs

us m

ariti

mus

Polarb

ear

Chuk

chi/B

eringSe

aSt

ock

(U.S.F

ishan

dW

ildlifeSe

rviceMar

ineMam

mals

Man

agem

ent2

002;N

OAA201

0b)

Neg

ative

Alask

anSto

ck(U

.S.F

ishan

dW

ildlifeSe

rviceMar

ineMam

mals

Man

agem

ent2

002)

Neg

ative

Wrang

elIs

land

State

Natur

eRe

serv

e(D

eroc

here

t al.19

97)

Neg

ative

Sout

hern

Bea

ufor

tpop

ulation

(IUCN

200

1;IU

CN/S

SCPolarBea

rSpe

cialistG

roup

20

10)

Neg

ative

Wes

tern

Hud

sonBa

ypo

pulatio

n(A

ars

et a

l.20

05)

Neg

ative

Sout

hern

Hud

sonba

ypo

pulatio

n(O

bbard

et a

l.20

07)

Stab

le/Po

sitiv

e

Nor

ther

nbe

aufo

rtsea

pop

ulation

(Stir

ling

et a

l.20

07)

Stab

le/Po

sitiv

e

Baffi

nBa

y(IU

CN/S

SCPolarBea

rSpe

cialistG

roup

201

0)Neg

ative

Dav

isstrait

(IUCN

/SSC

PolarBea

rSpe

cialistG

roup

201

0)St

able/Po

sitiv

e

Page 52: The Arctic Species Trend Indexlibrary.arcticportal.org/1665/1/ASTImarine.pdfThe Arctic Species Trend Index (ASTI) tracks the temporal abundance in 890 populations of 323 vertebrate

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