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Experimental evidence that feral cats cause local exti Experimental evidence that feral cats cause local exti

Experimental evidence that feral cats cause local exti - PDF document

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Experimental evidence that feral cats cause local exti - PPT Presentation

K Frank 12 Chris N Johnson Joanne M Potts Alaric Fisher Michael J Lawes John C Z Woinarski Katherine Tuft Ian J Radford Iain J Gordon 89 MaryAnne Collis 10 and Sarah Legge 6211 School of Biological Sciences University of Tasmania Private Bag ID: 86440

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IntroductionAlmostaquarteroftheworldÕsterrestrialmammalspeciesarethreatenedwithextinction(Hoffmannetal.2011;Dietal.2012),mainlyduetohabitatloss,habitatdeg-radationandoverhunting(Schipperetal.2008).Small-andmedium-sizedinvasivepredators,notablyferalcatsFelissylvestriscatusandblackratsRattusrattus,havecauseddeclinesinsmall-mammalpopulations,butsofarthishasmostlybeendocumentedonsmallislands(Nogalesetal.2004;Bonnaudetal.2011).Thepowerfuleffectofpredatorsonislandfaunasmaybeexplainedbyseveralfac-tors:(1)small-to-medium-sizedintroducedpredatorsoftenoccurathighdensitiesonislands;(2)nativeanimalsonislandsmaybenaõvetopredators,and(3)nativespeciesmayhavelowtotalpopulationsizes;and(4)largermam-malianpredators,whichcanreducetheimpactofsmall-tomedium-sizedpredators(Ritchie&Johnson2009),areabsentfrommanyislands.Additionally,thedateofarrivalofnon-nativepredatorsisoftenbetterdocumentedonislands,allowingformoreaccuratedocumentationofcausesandresponsesthanonthemainland.Catshavebeenspreadworld-widebypeople(Denny&Dickman2010),andwhileitiscleartheyhavecausedextinctionofmanyvertebratespeciesonislands(Dickman1992;Bonnaudetal.2011;Medinaetal.2011;Loss,Will&Marra2013),thereismuchlessevidenceforimpactoncontinentalfaunas(Woods,McDonald&Harris2003;Loss,Will&Marra2013).ArecentstudybyLoss,Will&Marra(2013)intheUnitedStatesshowedthattheimpactoffree-rangingcatsislikelytobemuchhigherthanpreviouslythought,withmorethan20billionmam-malskilledbycatseachyearintheUnitedStatesalone.TranslatedtoAustralia,thisimpliesapotentiallysigniÞ-cantimpactofcatsoncurrentlywidespreadsmall-mammalspecies.Sincethe15thcentury,Australiahaslostmoremam-malspecies(atleast23)thananyothercontinent,accountingforapproximatelyone-thirdofallrecentglo-balextinctionsofmammals(Johnson2006).Manyoftheseextinctionshavebeenattributedtoinvasivepreda-tors,especiallytheredfoxVulpesvulpes(Johnson2006).AlthoughAustraliaÕsCommonwealthThreatAbatementPlanforpredationbyferalcats(2008)lists36mammalsasthreatenedbycats,evidencelinkingferalcatstopastmammalianextinctionsisequivocal(Denny&Dickman2010),exceptinafewinstancesonAustralianislands(Dickman1992).Untilrecently,thetropicalsavannasofnorthernAustraliaseemedtobeunaffectedbythedeclinesandextinctionsthatoccurredamongmammalsofthecentralaridzoneandsouthernAustralia(Woinarskietal.Thiswasattributedprimarilytotheabsencethereoffoxes.However,smallmammalsarecurrentlydecliningacrossmuchofnorthernAustralia(Woinarskietal.2011a;Fisheretal.2013).Sixspeciesareatimminentriskofextinction,andmorethan20species(of40speciesinthesmall-to-mediumbodysizerange)havesufferedseverereductionsingeographicrange(Fitzsimonsetal.Thereareindicationsthatferalcatsmaybeatleastpartlyresponsibleforthesedeclines(Fisheretal.2013).Forexample,thespeciesdecliningmostseverelyareinthepreferredprey-sizerangeofferalcats(1500g)andoccupyrelativelyopenhabitatswhereexposuretopreda-tionislikelytobehigh(Fisheretal.2013).SpeciesthataredecliningacrossthemainlandofnorthernAustraliamostlyhavestablepopulationsoncat-freeislands,buthavedeclinedonislandswherecatshaverecentlybeenintroduced(Dickman1992;Woinarskietal.2011b).ThisevidenceoftheeffectofcatpredationiscounteredbythefactthatcatshavebeenpresentinnorthernAustraliaforatleast100years,andaviewthattheabundanceofferalcatsinAustraliaÕstropicalsavannasisgenerallytoolowtoaccountformajordeclinesaffectingmanyspeciessimultaneouslyoverlargeareas(Bradshawetal.Here,weprovidetheÞrstexperimentaltestoftheeffectofcatpredationondemographyofsmallmammalsinnorthernAustralia.Weusedareplicatedexperimenttodirectlymeasuretheimpactofferalcatsonthesurvivalandpopulationgrowthratesofasmall-mammalspecies,whileaccountingforthepotentialeffectsoftheothermammalianpredatorinthearea,thedingoCanisdingousingcamerastomonitorpredatoractivity.Theexperi-mentalenclosureswerelocatedintropicalsavannatypicalofenvironmentsthathaverecentlyexperiencedsmall-mammaldeclines(Woinarskietal.2011a),andinwhichsmall-mammalabundanceisnowverylow(SarahLegge,unpublisheddata).Previousmonitoringintheareasug-gestedthatcatdensitywastypicalofthelow-densitypop-ulationsthatoccurelsewhereinnorthernAustralia03km,Ridpath1990;KatherineTuft&SarahLegge,unpublisheddata).Wemonitoredthefateofsmall-mam-malpopulationsthathadbeenintroducedintotwopaired5ha)enclosuresinnaturallandscapesthatwereeitherexposedtoorprotectedfromcats,testingthepredictionthatpopulationgrowthratesandsurvivalwouldbesignif-icantlylowerinthepredator-accessiblethanthepredator-inaccessibletreatments.MaterialsandmethodsSTUDYSITEThisstudywasconductedatWongalaraWildlifeSanctuaryS,134E),a192200hareserveintheNorthernTerri-tory(NT),Australia.WongalarawasapastoralpropertygrazedatlowintensitybycattleBostaurusxindicus,buffalo,horsesEquuscaballusanddonkeysEquusasinus,untilitwasacquiredbytheAustralianWildlifeConservancy(AWC)in2006.Managementhassincefocussedonremovalofgrazingungulates,andÞremanagementdesignedtoreducethesize,intensityandfrequencyofÞres.Theonlymammalianpredatorapartfromtheferalcatcurrentlypresentisthedingo;dingoesweresuppressedbypoisonbaitingbeforethepropertywasacquiredbytheAWC,butarenowuncontrolled.2014TheAuthors.JournalofAppliedEcology2014BritishEcologicalSociety,JournalofAppliedEcology,1486Ð1493Feralcatsextirpatesmallmammals I,trappingcommenced2monthsafterreleaseofrats.Seventrap-pingsessionsofbetweentwoandfourconsecutivetrapnightswerecarriedout(24trapnightsintotal).InEnclosureII,trap-pingcommenced6monthsafterthereleaseofratsbecauseoflimitedaccessduringthewetseason.Inthisenclosure,ninetrap-pingsessionsofbetweentwoandfourconsecutivenightsoccurred(29nightsintotal;TableS1,Supportinginformation).Ateachcapture,individualswereidentiÞed,weighedandsexed.BodyconditionwasscoredusingthemethodofUllmann-e&Foltz(1999),fromcategory1emaciatedtoobese.Recruits(i.e.individualstrappedintheenclosuresthatwerenotpartoftheinitialrelease)werePIT-taggedatÞrstcap-ture.Anyuncollaredratslargerthan100gwereradiocollared,resultingin49rats(EnclosureIlow:7,high:13;EnclosureIIlow:13,high:16)beingradiocollaredandtrackedoverthecourseofthestudy.DETECTIONOFPREDATORSWeusedheat-in-motioncameras(ReconyxPC800HyperÞre,Hol-men,WI,USA)andweeklyvisualinspectionsfortracksandscatsinthesoftsoilaroundtheinsideandoutsideoftheperimeterfencestodetectpredators.Atleastthreecameras(butupto13andalwaysthesamenumberofcamerasatatime)wereplacedinsideeachhalfoftheenclosure,andonecamerawasinstalledateachsideontheoutsideofthefencesofeachenclosure(Fig.1).Cameraswereun-baited,toavoidattractingpredators.ANALYSISToestimatepopulationsizeandindividualsurvivalofrats,cap-recapturedatawereanalysedusingPollockÕsrobustsurveydesign(Pollocketal.1990).Trappingdatawereusedtocreateindividualencounterhistoriesforeachratindicatingcapture(1)ornon-capture(0)duringeachsamplingoccasion.DatawereanalysedusingaHugginsmodelwitharobustdesigninprogramv7.1(White&Burnham1999)andplottedusing(http://cran.r-project.org).Therearemultipleprimarysamplingperiods(i.e.repeatednightsofsamplingduringatrappingepisode)inPollockÕsrobustsurveydesign,whichareseparatedbylongerperiodsoftimeduringwhichthepopulationisopentogains(birthsandimmigration)andlosses(deathsandemigra-tion).Dataineachprimaryperiodarepooledtoestimatesur-vivalprobability,betweenprimarysamplingperiods.Withineachprimarysamplingperiod,thereareseveralsecondarysam-plingperiodsseparatedbyashortperiodduringwhichthepopu-lationisassumedclosed.DatafromeachsecondarysamplingperiodwereusedtoestimatetheprobabilityofÞrstcaptureandrecapture.Althoughrobustdesignmodelscanbeusedtoestimateprobabilitiesofmigrationintoandoutofthestudyarea,hereweÞxedthemigrationparameterstozero.Thiswasduetothepresenceofafencethatprecludedanimalmovement(i.e.probabilityofemigration,,andprobabilityofremainingawayfromthestudyareaiftheindividualhadpreviouslyemigrated,).ToensureparameteridentiÞcation,weassumedtheprobabil-ityofÞrstcaptureandprobabilityofrecapturewereconstant(.)withineachtrappingsession.Forwardmodelselectionwasused,wherebythesimplestnullmodelwasÞtted(i.e.(.)),representingconstantsur-(.),constantprobabilityofcapture(.)andconstantprobabilityofrecapture(.),aswellasnobehaviouraleffectonthecaptureprocess,thatis,chanceofÞrstcaptureisthesameaschanceofrecapture().ModelcomplexitywasintroducedbyÞrstinvestigatingwhethertherewasabehaviouraleffectinthecaptureprocess(i.e.)oraseasonaleffect(i.e.(session).(session)model),andthenwhethercovariatesinßuencedsurvival(i.e.thegrouptowhichtheindividualbelonged,eitherreleasedorrecruitedonsite,asessioneffect,sex,andwhetheritwasinthelow-orhigh-fencetreatmentoftheenclosure).Modelselec-tionusedAkaikeÕsinformationcriterionadjustedforsmallsam-plesize(AICc).ModelswereassumedequivalentiftheAICcvaluedifferedbylessthan2fromthemodelwiththelowestAICc(Burnham&Anderson2002).Todescribefactorsaffectingsurvival,15candidatemodelswerechosenaprioriandÞttedsep-aratelyforEnclosureIandEnclosureII(TableS2,Supportinginformation).Survivalofradiocollaredratswasanalysedasmeannumberofmonthstrackedwhileknowntobealive(indicatedbylastloca-tionchange),andthiswascomparedbetweencompartmentsforeachenclosureusingtwo-tailed-testsinMicrosoftExcel2010.Homogeneityofvariancewastestedusingan-test.Bodycondi-tionandreproductivestatuswerecomparedbetweentreatmentsbycomparingweightchangesbetweenthereleaseandÞrsttrap-pingsession,alsousingtwo-tailedUsingcameratrapdata,wecalculatedanactivityindexinv3.0.3formammalianpredatorsbydividingthenumberofencountersbythenumberofcamerastoaccountformalfunction-ingcameras.Thisindexwascalculatedforeachnight,thenaver-agedmonthlyandreportedwith95%binomialconÞdenceintervals.Wealsorecordedallinstancesofpredatoroccurrencesinsidetheenclosuresandaveragedhowregularlytheseoccurred.PREDATORACTIVITYANDINCURSIONSCatsorsignsofcatswereneverdetectedinsidethehigh-fencetreatmentofeitherenclosure.However,cattracksweredetectedinsidethelow-fencetreatmentofEnclosureIlessthan1monthafterratswerereleased(Fig.2).Atleasttwoindividualcatsweredetectedoncameraatthatsite4weekslater(Fig.2).Thereafter,catdetectionsrecurred,onaverage,everyweek(JuneOctober2012:9dayintervals;October2012April2013:60dayinter-vals)inthelow-fencetreatmentofEnclosureIuntiltheendofthestudy.Therewasalongerdelayofnearly1yearbeforecatswereÞrstdetectedinsidethelow-fencetreatmentofEnclosureII(Fig.3);duringtheentiresurveyperiod,therewereonlytwocat-detectioneventsoftwodifferentindividualsinsidethistreatment.DingoesorsignsofdingoeswereneverrecordedinsideeitherEnclo-sureIorIIineithertreatment.Cameratrapsontheoutsideoftheenclosuresindicatedthatingeneral,dingoactivitywassimilartocatactivityoutsideEnclosureI(Fig.S2a,Supportinginformation),whileoutsideEnclosureII,dingoactivitywasvariableandgreaterthancatactivityforthedurationofthestudy(Fig.S2b,Supportinginformation).CatactivitywassimilararoundEnclosureI(Fig.S2a,Supportinginforma-tion)andEnclosureII(Fig.S2b,Supportinginformation).2014TheAuthors.JournalofAppliedEcology2014BritishEcologicalSociety,JournalofAppliedEcology,1486Ð1493Feralcatsextirpatesmallmammals recordedbytheendofthestudyperiod,whilelittlerecruitmentwasrecordedinthelow-fencetreatment(Fig.2).Similarly,capturesofrecruitedratsatEnclosureIIwerealwaysmuchhigherinthehigh-fencecomparedtothelow-fencetreatment,withatotalof39comparedtosixwild-bornindividuals,respectively(Fig.3).Weestimatedtheabundanceofeachgroupofrats(i.e.releasedorrecruited)foreachtreatmentfromeachenclo-sureusingthemodelwiththelowestAIC.ForallratsatEnclosureI(Fig.2),abundanceinthelow-fencetreat-mentwasestimatedaszerofromtheÞrstsamplingperiod(2monthsafterrelease)untilourstudyceased.Theabun-danceofallreleasedratsinthehigh-fencetreatmentofEnclosureIdeclinedslowlyoverthe12monthsfollowingtheirrelease(Fig.2).TheabundanceofratsatEnclosureIIdeclinedmorerapidlyinthelow-fencethaninthehigh-fencetreatment(Fig.3).Threeofthefourradio-trackedfemalesinthelow-fencetreatmentweredeadwithin2monthsoftheirrelease,andneitheroftheuncollaredratswaseverrecaptured.AftertheÞrstsightingofcatsinthelow-fencetreatment,about1yearaftertheratswerereleased,thelastreleasedfemaleratwasmissingandthepopulationabundancedeclinedby75%.Afterthesecondcatdetection,noratswererecordedinthelow-fencetreat-ment(Fig.3).Radiocollaredratswereneverrecordedmovingoutsidetheenclosures.Whileweoccasionallyfoundrattracksalongtheperipheryoftheenclosures,werecordednoevi-denceofratstryingtoexittheenclosure.InEnclosureI,therewasasigniÞcantdifference(14,d.f.001)intheknownminimumsurvivaltimeofradio-collaredadultratsinthelow-fencetreatment(126months)comparedtothehigh-fencetreatmentSE034months).ForEnclosureII,therewasnodetecteddifferenceintheknownminimumsurvivaltime25,d.f.23)betweenthelow-fenceSE12months)andhigh-fence(69months)treatment(Fig.S4,Supportinginformation).Oftheradiocollaredratsassumedorknowntobedeadattheendofthestudy,thecorpsesofonly50%(threeoutofsix)wererecoveredfromthehigh-fencetreatmentand43%(threeoutofseven)fromthelow-fencetreatmentofEnclosureI,and55%(Þveoutofnine)inthehigh-fencetreatmentand25%(threeoutof12)inthelow-fencetreatmentofEnclosureII.Onaverage,thebodyconditionofratsintheenclosureswasÔwellconditionedÕ(categoryBC3;Ullmann-CullerFoltz1999).WeightsofreleasedrecapturedratsinEnclo-sureIincreased26%duringthe2monthsbeforetheÞrsttrappingsessioninthehigh-fencetreatment(Fig.S4,Supportinginformation);weightchangesinthelow-fencetreatmentofEnclosureIcouldnotbeassessedasratswerenotrecapturedafterrelease.Overthe6monthsbetweenthereleaseandtheÞrsttrappingsessioninEnclosureII,themeanweightsofreleasedrecapturedratsincreasedby71%inthelow-fencetreatmentand40%inthehigh-fencetreatment.ThemeanweightsofratsinthetwohalvesoftheenclosuredidnotdiffersigniÞcantly42,d.f.18).SurvivorshipoftheÞvewild-bornratswassimilartotheÞrst-generationanimalsbredincaptivity(threeoftheÞvewildratsdiedwithinamonthofrelease,onediedwithinsix,andthelastwildratdiedwithin8monthsofrelease).DiscussionWefoundamarkeddifferenceinthesurvivalandpopula-tiongrowthrateofratsbetweenthelow-andhigh-fencetreatments.Thiswasevidentlyduetopredationbycats.Populationdeclineswerecloselyrelatedtoincursionsbycats.Therewasnoevidencethatdingoeseverenteredanyenclosure,andavianandreptilianpredators(snakesandgoannas)wouldhavebeenequallylikelytoenterallcom-partments.Ratsinourexperimentalenclosuresmain-tainedgoodbodyconditionthroughoutthestudyperiod.Therefore,differencesinsurvivalwerenotrelatedtofoodlimitationorstressfromtheindirecteffectsofpredation.Inbothreplicates,ratswereextirpatedfromlow-fence(hereaftercalledÔcat-accessibleÕ)butnothigh-fence(here-aftercalledÔcat-inaccessibleÕ)treatments.However,thedemographicmechanismsleadingtoextirpationdifferedinourtworeplicates.InEnclosureI,reducedsurvivalinthecat-accessibletreatmentcausedrapidextirpationwithin2monthsofreleasingtherats;inEnclosureII,lowerlevelsofcatpredationandalowrecruitmentratebytheratsinthecat-accessibletreatmentcausedamoregradualdeclineintheratpopulationover15years.Althoughwewereunabletodeterminecauseofdeathofindividuals,itwashighlylikelythatcatswerethecauseoftheirultimateextirpation.AlthoughtheratpopulationswereconÞnedtofencedareas,ourenclosureswerelargerelativetothehomerangesizeofindividualrats(asindicatedfromourradiotrackingresults)andofferedsuf-Þcientspaceforratstoshelterindensevegetation,logsandhollowtrees.Thus,eventhoughcatsoccuratlowpopulationdensitiesintropicalsavannasofnorthern Table1.ModelselectionresultsforthetopthreeÞttedmodels(accordingtoAIC)toEnclosureIandEnclosureIIdata(fullresultsareavailableinTableS2,SupportingInformation).Fourcovariateswereinvestigated:thetreatment(lowf=low-fence),asessioneffect(,i.e.timebetweenprimaryoccasions),whethertheanimalsbelongedtothecaptive-bredorrecruitedgroup(andsexoftherat().Chanceofcapturewasassumedequaltothechanceofrecaptureandbothwereassumedtobeconstant(.).Migration()wasassumedtobezeroModelAICcdAICcNo.Par.DevianceEnclosureI(.)5147503508(sess)523298539504(.)523648893517EnclosureII(.)73293010712(.)7331502211710(.)7425896537362014TheAuthors.JournalofAppliedEcology2014BritishEcologicalSociety,JournalofAppliedEcology,1486Ð1493Feralcatsextirpatesmallmammals 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le.Fig.S1.ThefencedesigninEnclosureIandEnclosureII.Fig.S2.DingoandcatactivitysurroundingEnclosureIandEnclosureII.Fig.S3.Meanvegetationcoverinpercentat10cmaboveFig.S4.Survivalofradio-collaredreleasedrats.Fig.S5.WeightchangesofallratsbetweentheirreleaseandtheÞrsttrappingsession.TableS1.Summaryofreleaseinformationandtrappingoccasions.TableS2.Resultsofallselectedmodels.2014TheAuthors.JournalofAppliedEcology2014BritishEcologicalSociety,JournalofAppliedEcology,1486Ð1493Feralcatsextirpatesmallmammals