araneae biodiversity in the amazonian foothills: an
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SIT Graduate Institute/SIT Study Abroad SIT Graduate Institute/SIT Study Abroad
SIT Digital Collections SIT Digital Collections
Independent Study Project (ISP) Collection SIT Study Abroad
Fall 2019
Araneae Biodiversity in the Amazonian Foothills: An analysis of Araneae Biodiversity in the Amazonian Foothills: An analysis of
family and guild presence across habitat types family and guild presence across habitat types
Rae Lewark SIT Study Abroad
Follow this and additional works at: https://digitalcollections.sit.edu/isp_collection
Part of the Biodiversity Commons, Environmental Indicators and Impact Assessment Commons,
Forest Sciences Commons, Research Methods in Life Sciences Commons, and the Zoology Commons
Recommended Citation Recommended Citation Lewark, Rae, "Araneae Biodiversity in the Amazonian Foothills: An analysis of family and guild presence across habitat types" (2019). Independent Study Project (ISP) Collection. 3265. https://digitalcollections.sit.edu/isp_collection/3265
This Unpublished Paper is brought to you for free and open access by the SIT Study Abroad at SIT Digital Collections. It has been accepted for inclusion in Independent Study Project (ISP) Collection by an authorized administrator of SIT Digital Collections. For more information, please contact [email protected].
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AraneaeBiodiversityintheAmazonianFoothillsAnanalysisoffamilyandguildpresenceacrosshabitattypes
Lewark,RaeAcademicDirector:Xavier,SilvaPhD
ProjectAdvisor:GermaniaEstevez,PhDFieldAdvisor:AlexBentleyHawaiiPacificUniversityEnvironmentalStudies
SouthAmerica,Ecuador,PastazaProvince,EcomingaRioAnzuSumakKawsayinSitu
SubmittedinPartialFulfillmentoftherequirementsforEcuador:ComparativeEcologyandConservation,SITStudyAbroad,Fall2019
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AbstractTheactivityoftheorderAraneaewithinecosystemsisoftenconsideredanecologicalmystery.Consideredtop-leveltrophicpredators,spidersactasregulatorsofinsectpopulationsandhaveinfluenceuponthefoundationofthetrophicweb.IntheEcuadorianAmazonianfoothills,itisimportanttoaddressthelackofknowledgeofthebiodiversityofspidersintheregion.Conductingbiodiversitystudiesacrosslandusegradientscanbegintocharacterizeanthropogenicimpactsonneotropicalspiderspecies.ThisstudyquantifiesthearaneaebiodiversityinthetransitionbetweentheCloudandAmazonforestsinEcuador.Populationsinprimaryforest,secondaryforest,cultivatedfieldsandcavesystemswereanalyzedtoidentifythefamiliesandguildspresentintheecosystems.Thebiodiversityofspiderfamiliesandguildtypewerefoundtodiminishwithincreasinglanduseimpactandthedecreaseofvegetationcomplexity.ResumenLaactividaddelordenAraneaeentrelosecosistemasfrecuentementeseconsideraunmisterio.Consideradepredadoresimportantesarañassonreguladoresdelaspoblacionesdeinsectosytieneninfluenciasobrelabasedelaredtrófica.PorlasestribacionesdelaAmazonia,esimportanteaenfocarenlafaltadeinformacióndelabiodiversidaddearañasenelregión.Larealizacióndemásestudiosentrelosgradientesdelusodelatierrapuedeempezaracaracterizarlosimpactoshumanosenlasarañasdelosalotrópicos.EsteestudiocuantificólabiodiversidaddearaneaeenlatransicióndelBosqueNubladoylaAmazoniandeEcuador.Laspoblacionesdebosqueprimario,bosquesecundario,camposcultivados,ylossistemasdecuevasfueronanalizadosaidentificarlasfamiliasylosgremiosquesepresentenenlosecosistemas.Labiodiversidaddelasfamiliasylosgremiosdearañasseencontraronadisminuirconelcrecimientodelusodetierrayconeldecrecimientodelacomplejidaddelavegetación.AcknowledgementsTheauthorwouldliketoextendgratitudetoGermaniaEstevezforadvisementandguidancethroughoutthestudy,toAlexBentleyforadvisementinthefieldandAnaMariaOrtez,XavierSilvaandDianaSerranoforaidthroughoutthedevelopmentandcompletionofthestudy.TothestaffofSumakKawsayinSituandthefellowAnzuteamresearchers,ReneeHeller,TeoCarr,andZaneLibkefortheircompanionship,theirresilienceandtheirconstantabilitytoinspireeveninthehardestconditions.ToalltherepresentativesofSITstudyabroad.IntroductionSpidersrepresentamegadiverseorderwithinthearthropodphylum,with48,262currentlydescribedspecies(TheWorldSpiderCatalog20.5).Spidersposeataxonomicchallenge,asmorphologicalvariationwithinspeciesisabundantandcanbeduetogeneticdeviationorgeographicaldifference(Coddington&Levi1991).Thecurrentnumberofdescribedspeciesisspeculatedtoonlyconstitute35%ofthetotalspiderspeciespresentonearth.Incomparisontoothernon-invertebrategroups,spidersandotherarachnidsrepresentbothalackofresearchandanareafornewdiscovery(Pinzon2010,Brooks2004.)Whileresearchintotheecologicalimportanceofspidersisincreasing,onlyanaverageof605newspeciesaredescribedeachyear.Atthisrateofdescription,itwouldtakemorethan150yearstodevelopasufficientdatabaseontheplanet’sspiderbiodiversity(Platnick2013).Intheneotropics,wherebiodiversityisnotablyhigherthantemperateregions,researchintospiderbiodiversityisneededand
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presentsafrontierforthediscoveryanddescriptionofnewspecies.SpidersoftropicalregionssuchasinEcuador,presentanunder-exploredworldofecologicalandphysiologicalpotential(Basset2012.)Spidervenomcontainsneurotoxinsthatarebecomingimportantinneurobiologicalinnovation,studiesintopropertiesofspiderwebforfiberresearch,andalsointhedevelopmentoflessenvironmentallydamaginginsecticides(Coddington&Levi1991).Spidersmaybenefittheeffectivenessofpestcontrolinagroforestry.Increaseddiversityofspiderpopulationshasbeenfoundtobenefitthemitigationofpestimpactoncrops.Arangeofspeciesfromdifferentguildscreatesaneffectivenetworktotargetpestsacrosstheirlifecycles.Thispromoteslandmanagementwithlesschemicalimpactandfocusesonharnessingthenaturalecosystemtopromotecropproductivity(Marc&Conrad1997).Inordertoquantifytheimpactoflanduse,spiderpopulationsmustbethoroughlysurveyed.Themosteffectivetechniqueforspidercollectingis“nocturnalhandcollecting.”Thisisduetohigherprobabilityofencountersinthenighthourswhenmanyspeciesaremorelikelytobehunting.ThisstudyfocusedonhandcollectingasthemainsamplingmethodasadvisedbyRego(2009)whenothermethodsarenotavailable.Thismethodwasthefocusofthestudyinordertoencounterarangeofspidersacrossguildsandvegetationtypes,aswellastoobserveeachindividual’secologicalinteractionsandbehaviorwhileintheirnaturalenvironments.Nightcollectingsessionswereavitalcomponentofthestudyasspidersareoftenobservedinhigherquantityinhoursofnolightintheneo-tropics,withsomespeciesexclusivelyrecordedasnocturnallyactive(Green1999).Thisisoftenduetospider’smainpredatorsbeingactiveduringdaylighthours,andinordertohuntspidersmustputthemselvesatrisk.Buildingaweborambushhuntingdemandshighlevelsofenergyandrequiresindividualstoleavelocationswheretheyaresafefrompredators(Venner2005).Huntinginlowornolighthoursdecreasestheriskofpredationandalsoincreasestheindividual’spotentialforcatchingunsuspectinginsectswhomaynotbeabletodetectthespider’spresenceaswellatnight(Rypstra1986).Spidersareconsideredtopleveltrophicpredatorswithintheirhabitats.Spidersfilltheecologicalregulatorrolewithintheirecosystems,withthecapacitytodictatethecompositionandbalanceofinsectpopulations(Martin1982).Throughouttheplanet’secosystems,predatorsaredistinguishedaskeystonecomponentsinoverallhealth.Thedisproportionatelackofresearchintospider’simpactonecosystemfunctionalitydrawsastarkcomparisontopredatorsonlargertrophiclevels.Whilesmallinphysicalsize,spidershavethecapacitytoactasimportantcontrolagentsinthebalanceofinsectpopulations(Silva1992).Spiderfamiliespresentadiverserangeofguilds.Guildsareclassifiedasgroupsofspecieswhocompeteforthesameresourcesinanecosystem.Identifyingtheguildspresentinanecosystemcanleadtoabetterunderstandingoftheecologicalimpactspidercommunitiesarehavingonthetrophicweb.Classifyingguildscanalsodevelopanunderstandoftheimpactoflanduseinahabitat.ThedescriptionsofspiderguildsbyCardosoetal(2011)characterizedspiderguildsby8definitions:sensingwebweavers,sheetwebweavers,spacewebweavers,orbwebweavers,specialists,ambushhunters,groundhuntersandotherhunters.
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Thestratosphericrangeofaspidercanhelpidentifythetaxonomyaswellastheguilditbelongsto(Yanoviak2013).Spidersthatrelyonspecificvegetationstructureforwebbuildingorforhuntingwillbemorevulnerabletochangesinvegetation.Spiderswhorelyoncamouflageforhuntingmayalsobenegativelyimpactedbychangesinvegetationtype(Thery2002).Spiderswillutilizevegetationstructuretobuildwebs,forage,oruseambushhunting.Webbuildingspiderswillelectlocationsofhigherinsecttraffic,inlocationswheretheycanattractspecificindividuals,orlocationswheretheycanutilizesurprisetoentrapprey(Venner2005).Thisstudycollectedspecimensacrossfourdistincthabitats.Withineachhabitata200mtransectorientedaroundabodyofwateranda200mtransectinadryregionweresampled.Thefourecosystemssampledwereprimaryforest,secondaryforest,cultivatedfields,andsubterraneancaves.Thefirstthreeecosystemtypeswereselectedinordertocomparethebiodiversitygradientacrosstheregionwithincreasinganthropogenicimpact.Thecavetransectswereselectedinordertoobservetheimpactsoftheecologicalpressuresofsubterraneanecosystemsonspiderdiversity(Mammola&Isaia2017).Theprimaryforesttransectswereconsideredregionsunalteredbyanthropogenicactivity,withlittletonodisturbance.Thefirsttransectselectedwassituatedinavalleyandcutthroughthepathofastream.Thesecondtransectselectedwassituatedalongtherideofthesamevalley,andcutthroughtheforest.Bothtransectshadlittletonohumanimpactexceptforcollectingreasons.Thestructureofvegetationhasasignificantimpactonspiders.Astheyrelyheavilyoninfrastructureforhunting,areaswithmorediverseflorawilloftenprovidethefoundationfordiversespiderpopulations(Schüpbach2013).Thesecondaryforesttransectsweredefinedasareaswereprimaryforesthadbeencleared,buthadthenbeenabandonedandsuccessionalgrowthwaspermitted.Thefirsttransectselectedwasorientedclosetoariveralongastreamtributary.Thesecondtransectcutthroughtheforest,andcrossedthedryportionofthefirsttransectsstream.Secondaryforestgrowthisdenserwhilelessdiversethanprimaryforests,andiffoundadjacenttoprimaryforestswilloftenpresentidealconditionsforspiderdiversity(Floren&Deeleman-Reinhold2005).Thecultivatedtransectswerecharacterizedasareaswhereprimaryforesthadbeenremovedtoopenthelandforagriculturalactivity.Thetransectsselectedweredominatedbygrassesandsomesuccessionalforestflora.Cultivatedhabitatsoftenexhibitpatchworklikeregions,withthealtercationsoflandcausingfragmentationofhabitatsforthespeciespresent.Spidersareadaptivepredators,oftenexhibitingresiliencewhenimpactedbyhabitatdisturbance.Oftenabletoadapt,spidersthriveinareaswithhighinsectpopulations,suchasagriculturalsites,orhabitatsaroundbodiesofwater.Theycanadapttheirhuntingmethods,whetherweborientedorambushhunting,toalteredecosystems(Schüpbach2003).Ithasbeenobservedhoweverthatoveralldiversityofspecieswilldecreaseinareasofdisturbanceimpactedbyagricultureorotheranthropogeniclanduse.Thisusuallyresultsinafewspeciesthrivinganddominatingtheecosystem(Cardosoetal2011).
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Thecaveswerecharacterizedassubterraneangeologicalformations.Subterraneanhabitatscreateextremeenvironments,exposinginhabitantstohighlevelsofecologicalpressure.Duetolowresourceavailabilityaswellaslowlightlevels,specieslivingincaveecosystemswilloftenevolveawayfromtheirterrestrialcounterparts(Mammola&Isaia2017).ThisstudyaimedtoevaluatethebiodiversityofspidersinthetransitionalhabitatsbetweentheEcuadorianCloudForestandAmazonForest.Bydevelopinganunderstandingofthespeciesintheregionandbysamplingvarioushabitatstypes,theimpactofhumanlanduseonspiderdiversitywasalsoevaluatedacrossincreasinglevelsofaltercation.MethodsIntheFieldThestudywasconductedinNovember,2019inthetransitionbetweenthedryandthewetseasoninEcuador.ThestudysitewasintheRioAnzuregionofthePastazaProvince,intheEcomingaandSumakKawsaybiologicalreserves.Collectionsessionswereperformedfor16daysbetweenthe12thandthe29thofNovember.Thefourhabitatssampledwereprimaryforest,secondaryforest,cultivatedfields,andsubterraneancaves(cavesnotmapped).Foreachtypeofhabitat,excludingthecavesystems,two200mtransectswereused,onethatwasorientedaroundabodyofwater(wettransect)andonethatwasnotimpactedbywater(drytransect)(figure1).Thecavetransectswereevaluatedinsearchhoursinsteadofdistancesurveyed.
Figure1.Mapofthe6maintransects,TCM=cultivatedwettransect,TCS=cultivateddrytransect,TSMIandTSM2=secondarywettransects,TSS=secondarydrytransect,TPM=primarywettransect,TPS=primarydrytransect.
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Surveyingsessionsutilizedhandcollectingmethods,withemphasisonidentifyingindividualsaswellasobservingbehaviorandenvironmentalinteractionofeachmorpho-species.Whenanewindividualwasencountereditwasphotographed,theheightabovegroundwhereitwasfoundwasmeasured,andthetypeofvegetationorstratawasclassified.Vegetationorstrataclassificationwasbrokenupinto9categories:gravel/sand,surfaceofwater,soilbank/wall,leaflitter,rootsystems,fallentrees/branches,grass,low-levelfoliageandhigh-levelfoliage.Thepresenceofawebanditstypewasnoted,aswellasbehaviorwhendisturbed,eggsacktype,orothernotablefeaturesthatcouldbeusedinidentification.AsfoundbyAvezedoetalin2014,nocturnalhandcollectingisthemosteffectivemethodforcollectingspiderspecimensaboveothermethodssuchastreebeatingorpitfalltraps.Whileacombinationofthethreemethodsisideal,nocturnalhandcollectingisthemostsuccessfulespeciallywhenotheroptionsarenotaccessible.Thisisduetohigheractivityofspiderspeciesatnightcomparedtotheday(Green1999).Thisstudyaimedtomaptheactivityofdifferentspidergroupsthroughoutdifferentlightlevels,anddevelopedcollectingschedulesinnight,dayandtransitionallightsessions.Thisstudyutilizedhandcollectingastheprimarysamplingtechniquebecausepitfalltrapsandtreebeatingeitherkillsindividualsordisruptstheirnaturalactivity.Thisinhibitsobservationtoobserveoftheirecologicalinteractionandbehaviorintheirnaturalenvironment.Fifteencollectinghourswerespentineachtypeofhabitat,withevenamountsoftimespentcollectingintransitionalhours(sunriseandsunset),daylighthours,andnighthours.Thecavesystemsweresampledforonlyanequivalentofthreesamplingsessions,andnotsubjecttolightlevelspecificsampling.Atotalof45searchandcollectionhourswereperformedinthemainthreehabitattypes,and3hoursand45minutesinthecavetransects.Eachtransectwaswalkedslowly,withsweepingvisualsearchesdonefromsidetosideofthevegetationorwaterway.Leaflitter,soilbanks,fallentrees,rootsystemsandtheundersidesofleaveswerethoroughlyexaminedateachsearchinterval.Nighttimesessionsutilizedbothaheadlampandspottingflashlightinvisualsearches.Samplesweretakenatthreedifferentlevelsoflight.Daylightsamplesweretakenbetweenthehoursof8:00and17:00.Nightsamplesweretakenbetween19:00and0:00.Transitionallightsamplesweredividedevenlybetweenmorningandeveningtransitionhours,withmorningsessionstakingplacewithinthehoursof5:30and7:45,andeveningsessionstakingplacewithin17:15and18:45.Fifteenhoursofcollectingineachlightlevelwereperformedacrossthethreemainhabitats,withtransitionalhoursbrokeninto7hoursand30minutesforthemorningtransitionsand7hoursand30minutesfortheeveningtransitions.TheapplicationiNaturalistwasusedtoorganizedataduringcollectingsessions.Eachindividualwasphotographedinthefieldwithamacro10mmMomentLensattachedtoaniPhoneXR.Ifpossible,photosweretakenofeachindividualfromabovetocapturethelegandbodyoverallshape,alongthedorsalplanetocaptureshapeofthecarapaceandtheabdomen,andfromthefronttocapturetheocularpattern.Whenanewmorpho-specieswasfounditwascollectedtobepreservedandidentifiedoutsideofthefield.
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PreservationandIdentificationSampleswerepreservedina70%alcoholsolution,andphotographedwiththesamelensusedinthefield.Amicroscopewasusedforidentificationwhenmacrophotoswerenotsufficientforidentification.Thefamilyofeachindividualwasidentifiedaswellasthegenuswhenpossible.IdentificationwasbasedonthedescriptionsofJocqué(2007),Wegner(2011),Duperre(2013,2015,2016),Brescovit([nodate]),andtheWorldSpiderCatalog20.5(2019).GuildswereassignedtoeachfamilybasedonthedescriptionsofCardosoetal(2011).StatisticalAnalysisThediversitywithineachhabitataswellasthecompositediversityoftheregionwascalculatedusingtheentropyoftheShannonDiversityIndex,andtheinverseSimpsonDiversityIndex.TheShannonDiversityIndexwhichaccountsfortheincreaseofrarespecies,aswellastheabundanceandevennessinthecommunityandfunctionsonanordinalscale.Theentropywasappliedinordertoavoidunbalancedinfluenceofrareorcommongroupsdisproportionately(Jost2006).TheGini-SimpsonDiversityIndexdescribestheoveralldiversityofacommunity,accountingforrichness,evennessanddivergence(Solow1993).Theinverseoftheformulawasappliedinordertoaccountfordominanceofgroupswithinthesample(Jost2006).TheShannonIndexiscalculatedasfollows,where(p1)isthequantityofspecies“1”inrespecttothetotalnumberofspecies.
= 𝑒𝑥𝑝 &'(𝑝))|ln 𝑝)|.TheGini-SimpsonIndexiscalculatedasfollows,wherenisthetotalnumberofindividualsinaspecificspecies,andNisnumberofindividualsofthecumulativespecies:
= 1
0 1∑(𝑛𝑁)
45
ThesamplecompletenessofeachhabitattypeaswellastheregionasawholewascalculatedusingthesoftwareiNext(Chaoetal2016).Thisisanimportantmeasuretotakewhenstudyingarachnidpopulationsbecausetheyoftenpresenthighnumbersofsingleordoublemorpho-speciesencounters(singletonsanddoubletons)(Rego2009).Aspeciesaccumulationcurvewasmappedinordertocomparethenumberofspeciesfoundinaregioninrespecttotheeffortusedtofindthem(Chaoetal2016).TheJaccardIndexwasusedtomeasurethepercentsimilarityofmorpho-speciesbetweenthethreemainhabitatssampled(primary,secondaryandcultivated.)Theformulaoperatesbydividingthenumberofsharedspeciesbythetotalnumberofspecies,wherenequalsnumberofsharedspeciesandNequalstotalnumberofspeciesbetweenthehabitats.
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%𝑠𝑖𝑚𝑖𝑙𝑎𝑟𝑖𝑡𝑦 =𝑛𝑁
Thesamplescollectedfromthecavetransectswerenotstatisticallycomparabletotheotherhabitatsasthesamplingeffortwasdisproportionate.Theresultsfromdatasampledfromthecaveswasincludedinthediscussionportionofthestudy.Results&DiscussionAtotalof1036spiderswerecollectedacrossthefourhabitattypes.Thetotalnumberofindividualscouldbebrokenupinto150morpho-speciesand20families(appendixA).The20familiescouldbeclassifiedinto8guilds(table1).Ofthetotalmorpho-species4couldnotbeidentifiedandfallintotheunknownclassification.
Table1.SpiderFamiliesfoundacrossallhabitatsdesignatedintoguilds.Guild FamilyAmbushHunter Deinopidae
Thomisidae
GroundHunter CorinnidaeHeteropodidaeLycosidae
OrbWeaver AraneidaeSymphytognathidaeTetranathidae
OtherHunter AnyphaenidaeCtenidaeMiturgidaeSalticidaeScytodidae
SensingWeb Theraphosidae
SheetWeb AgelenidaePisauridae
SpaceWeb PholcidaeTheridiidae
Specialist DysderidaeGnaphosidae
Ofthe150morpho-species,onefromeachhabitatwasfoundtodominanttheirrespectivehabitattypes.Themostdominantmorpho-speciesfoundintheprimaryhabitatwasPisauridaegen.sp.1(15%),Thenextmostdominantmorpho-specieswere
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Pholcidaegen.sp1.andTetranathidaegen.sp.1makingup12%and11%ofthetotalpopulation,respectively.Themostcommonmorpho-speciesinthesecondaryhabitatwasPholcidaegensp2whichmadeup17%ofthetotalmorpho-speciesfoundinthehabitat.Thenextmostdominatemorpho-specieswereTheridiidaegen.sp.1andPholcidaegen.sp.2whichmadeup17%and13%ofthetotalmorpho-speciesfound,respectively.Themostcommonmorpho-speciesfoundinthecultivatedhabitatwasTetranathidaleucagesp.whichrepresented40%ofthetotalpopulation.ThefollowingdominantspecieswereTheridiidaegen.sp.1,andPisauridaegen.sp.2,makingup11%and8%oftheremainingpopulation,respectively.
Figure2.Thethreemostcommonmorpho-speciesfoundineachhabitattype.Fromlefttoright:themostabundantmorpho-speciesintheprimarytransects,secondarytransects,andthecultivatedtransect.Themostcommonmorpho-speciesinthesecondaryhabitatwasPholcidaegensp2whichmadeup17%ofthetotalmorpho-speciesfoundinthehabitat.Thenextmostdominatemorpho-specieswereTheridiidaegen.sp.1andPholcidaegen.sp.2whichmadeup17%and13%ofthetotalmorpho-speciesfound,respectively.Themostcommonmorpho-speciesfoundinthecultivatedhabitatwasTetranathidaleucagesp.whichrepresented40%ofthetotalpopulation.ThefollowingdominantspecieswereTheridiidaegen.sp.1,andPisauridaegen.sp.2,makingup11%and8%oftheremainingpopulation,respectively.Ofthethreemainhabitats,thecultivatedhabitatspresentedthehighestdominancebyonemorpho-specieswitha40%representationofTetranathidaleucagesp.Thismorpho-speciesisnotablyadaptedtocultivatedenvironments,andareproficienthuntersingrassdominatedecosystems(Hall2019).Similartospiderbiodiversityin
Pisauridae Pholcidae Tetranathidae
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othercultivatedareas,themostalteredenvironmenthadthehighestdominanceofasinglemorpho-species(Cardosoetal2011).ComparisonofDiversityTheShannonEntropycalculationsshowedhigherdiversityandevennessofthepopulationfromthecultivatedtotheprimaryhabitatgradient(table2).Anincreaseof61.31%wasfoundbetweenthecultivatedandsecondaryhabitats,andanincreaseof29.02%betweenthesecondaryandprimaryhabitats.Theincreaseof72.54%betweenthecultivatedtoprimaryhabitatswasthemostsignificantchangeinbiodiversity(appendixD).TheTransformedGini-Simpsoncalculationsshowedasignificantincreaseofbiodiversitywhenhabitattypeswerelessimpactedbyanthropogenicaltercation(table2).Anincreaseof67.23%wasfoundbetweenthecultivatedandthesecondaryhabitat,andanincreaseof33.31%betweenthesecondaryandprimaryhabitat.Theincreaseof78.15%betweenthecultivatedandprimaryhabitatswasthemostnotableinchangeinbiodiversityacrossthelandaltercationgradient(appendixD).Table2.Diversityvalues,foreachhabitattyperespectivelyandforallthreecombinedtorepresenttheregionalbiodiversity.Habitat ShannonEntropy Gini-SimpsonTransformedPrimary 3.86 25.58Secondary 2.74 17.06Cultivated 1.06 5.59Regional 2.88 51.91Thepercentsimilaritiesbetweenhabitatsshowedtheprimaryandcultivatedhabitatshadtheleastsimilaritysharingonly10%morpho-speciesbetweenthem.Secondaryandcultivatedshared31%ofthetotalmorpho-species,showingthegreatestsimilarity.Theprimaryandsecondaryhabitatshowedaslightlylowersimilaritywith28%ofthetotalmorpho-speciesshared(table3).
Table3.Jaccard’sIndicesbetweenthe3mainhabitatssampled.HabitatComparison Shared
Morpho-speciesTotalMorpho-species
JaccardIndices
PrimarytoSecondary 30 106 28%
SecondarytoCultivated 34 108 31%
CultivatedtoPrimary 15 143 10%
Habitatswithsimilarlanduseimpactssharedmoremorpho-species.Boththesecondaryandprimarytransectsshowedmoresimilarity,asitcanbeassumedthemorpho-speciesinthosehabitatsrelyonmoreunalteredvegetationstructuretosurvive.Morpho-speciesinthecultivatedregionsmaybeabletocrossovertoboththesecondaryandprimaryhabitats,butmanyoftheprimaryandsecondarymorpho-
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speciesmaybetoospecializedtotheirvegetationinfrastructuretosurviveinhighlyimpactedregions(Gollan2010).SpeciesAccumulationandSpeciesCoverageTheindividualsfoundacrossthethreemainhabitatsrepresentedfrom60%to75%ofthetotalexpecteddiversityoftheregion.Thisleavesanunidentifiedmarginfrom35%to40%ofmorpho-speciesnotaccountedforinthesamplingperiod(figure3).
Figure3.SpeciesAccumulationCurveofthethreemainhabitats:cultivated,primaryandsecondary.Theinterpolatedlinerepresentsdatacollectedandtheextrapolatedlinerepresentstheprojectionofspeciesandindividualsnotfoundinthehabitatsduringthestudy(Chaoetal2016).Thesamplingeffortsofthestudysuccessfullyaccountedforaround60%to75%ofthetotalspeciesinthehabitatssurveyed.Thisleavesanunidentifiedmarginfrom35%to40%ofthemorpho-speciesnotfoundinthesamplingperiod(figure4).
Figure4.SampleCoverageofthesurveysacrossthethreemainhabitats:cultivated,primaryandsecondary.Theinterpolatedlinerepresentsdatacollectedandtheextrapolatedlinerepresentstheprojectionofdiversitythatremainsun-surveyedinthehabitats(Chaoetal2016).
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Thisresultreflectsthefindingsofsimilarstudieswherearachnidbiodiversitystudiesofthisgeneralsizeareusuallyabletoaccountforaround70%ofthetotalregionaldiversity(Azevedoetal2014).Duetohighvariabilityamongstpopulations,itiscommontoencounterahighnumberofsingletonsanddoubletonswhilesurveyingarachnids(Rego2009).FamilyCompositionTheregionalfamilycompositionshowedthefamilyPholcidaehadthegreatestabundancerepresenting23.36%ofthetotalindividualsfoundacrosshabitats.ThisresultissimilartothefindingsofMoore(2015),whofoundPholcidaewasthemostabundantfamilyacrossaltitudesinanadjacentgeographicalregion.
Figure5.Examplesfromthe3mostabundantfamiliesintheregion,amorpho-speciesfromthePholcidae,TheridiidaeandTetranathidaefamily.ThefamiliesTheridiidaeandTetranathidaewerethesecondandthethirdmostabundantfamiliesrepresenting18.24%and17.95%ofthetotalregionalpopulation(appendixC.)ThefamilyTheridiidaewasfoundtobeabundantinEcuadorianCloudForestsbyRobinson(2018),inastudyonthebiodiversityofspidersacrossaltituderange.
26.20%25.56%
12.14%
8.63%6.07%4.47%3.00%2.88%2.56%2.00%1.28%1.28%1.00%1.00%0.96%0.96%0.64%0.32%
0.00%5.00%
10.00%15.00%20.00%25.00%30.00%
pholcidae
pisaurid
ae
tetran
athidae
theridiid
ae
saltic
idae
ctenidae
lycosid
ae
thomisidae
corin
nidae
heteropodidae
scytodidae
Unknwn
agele
nidae
anyp
haenidae
araneid
ae
theraphosid
ae
symphyto
gnath
idae
deinopidae
A) Primary Family Dominance Curve
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Figure6.TheFamilyDominanceCurvesofeachhabitattype,exhibitingthefamilieswiththegreatestrepresentationinthehabitat.ThemostcommonfamilyfoundintheprimaryhabitatswasPholcidae,whichrepresented26.20%ofthetotalindividualsfound.PisauridaeandTetranathidaemadeupthesecondandthirdlargestcomponentofthesample,representing25.56%and12.14%respectively.Theremaining14familiesandthefewindividualsthatcouldnotbeclassifiedintofamilieseachrepresentedfrom0.32%to8.63%ofthetotalcomposition(figure6A).ThemostcommonfamilyinthesecondaryhabitatwasPholcidaewhichrepresented38.44%ofthetotalindividualsfound.PisauridaeandTheridiidaemadeupthefollowinghighestpercentagesrepresenting33.13%and25%respectively.Therestofthefamiliesandthefewindividualswhocouldnotbeidentifiedrepresentedfrom0.31%to6.56%oftheindividualsinthehabitat(figure6B.)ThemostcommonfamilyinthecultivatedhabitatwasTetranathidaewhichrepresented40.18%ofthetotalindividualsfound.TheridiidaeandAraneidaemadeupthefollowinghighestpercentagesrepresenting21.11%and12.02%respectively.Therestofthefamiliespresentedfrom0.29%to10.26%oftheindividualsinthehabitat(figure6C.)
38.44%
33.13%25.00%
6.56% 4.06% 3.44% 2.1… 1.88% 1.25% 0.94% 0.94% 0.31% 0.31%0.31%0.00%5.00%
10.00%15.00%20.00%25.00%30.00%35.00%40.00%45.00%
Pholcidae
Pisaurid
ae
Therid
iidae
Araneidae
Tetra
nathidae
Thomisid
ae
Ctenidae
Saltic
idae
Scytopidae
Corinnidae
Lycosid
ae
Therophosid
ae
Anyphae
nindae
Unknwn
B) Secondary Family Dominance Curve
40.18%
21.11%12.02% 10.26%
5.57% 4.40% 2.93% 1.76% 0.88% 0.29% 0.29% 0.29%0.00%5.00%
10.00%15.00%20.00%25.00%30.00%35.00%40.00%45.00%
Tetra
nathidae
Therid
iidae
Araneidae
Pisaurid
ae
Saltic
idae
Ctenidae
Lycosid
ae
Corinnidae
Dysderid
ae
Deinopidae
Thomisid
ae
Unknwn
C) Cultivated Family Dominance Curve
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ForboththeprimaryandsecondaryhabitatsthePholcidaefamilydominatedthenumberofindividualsintheecosystem.ThisfindingwassimilartothefindingsofMoore(2015),whofoundinuncultivatedregionsthePholcidaefamilywasthemostabundant.Thecultivatedhabitathadthemostsignificantdominanceofasinglegroup(Tetranathidae)comparedtotheotherhabitatswhichshowedalmostequalpresenceofatleasttwofamilies(figure6.).TheabundanceoftheTetranathidaefamilyinthecultivatedareawassoapparenttheywereconsideredapartofthethirdmostabundantfamilyintheregion(appendixc.)
Figure7.TheCaveHabitatDominanceCurve,exhibitingthefamilieswiththegreatestrepresentationinthehabitat
Thepopulationsinthecavehabitatshowadramaticdominanceoftwogroups.ThefamiliesPholcidaeandGnaphosidaepresented96.67%ofthepopulation(figure7).Comparedtothethreemaintransectsthathadincreasedecologicalresources,thecavehabitatscouldonlysupportafewfamilies.Theresourcesandecologicalinfrastructureofcavehabitatsisinhospitabletomanyorganisms,andthepresenceofafewspecializedfamiliesisexpectedundersuchconditions(Mammolaetal2017).GuildCompositionAcrosstheregionthespaceweb,sheetwebandorbweaverguildswerethemostabundant.ThetwomostabundantfamiliesPholcidaeandTheridiidaeareclassifiedasspacewebbuilders,whilethethirdmostabundantfamilyTetranathidaehuntsintheorbweaverguild(table1).
60.00%
36.6667%
1.67% 1.67%0.00%
10.00%20.00%30.00%40.00%50.00%60.00%70.00%
Pholcidae
Gnaphosid
ae
Therid
iidae
Therap
hosidae
Cave Family Dominance Curve
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Figure8.HabitatGuildComposition,displayedinpercentagesoutofthetotalnumberofindividualssampled.ChartArepresentsprimaryguilds,ChartBrepresentssecondaryguilds,andChartCrepresentscultivatedguilds.Themostabundantguildintheprimaryhabitatwerespacewebbuildersmakingup35%ofthetotalguildsrepresented.Thesecondgreatestusagewasrepresentedbysheetwebbuilderswhomadeup26%oftheindividualsinthehabitat(figure8A).ThefamiliesbuildingspacewebsincludePholcidaeandTheridiidae(table1),withPholcidaerepresentingthehighestpercentageofindividualsinthehabitat.Themostrepresentedguildinthesecondaryhabitatwerespacewebbuilders,makingup53%ofthetotalindividualsinthehabitat.Thethreemostabundantmorpho-specieswereclassifiedasspacewebbuilders.Thesecondmostrepresentedguildweresheetwebbuilders,makingup28%ofthetotalindividualsinthehabitat(figure8B.)Thefirstandthirdmostabundantfamiliesinthehabitat(PholcidaeandTheridiidae)wereclassifiedinthespacewebguild,whilethesecondmostabundantfamilyPisauridaewasclassifiedinthesheetwebguild(table1).Themostrepresentedguildinthecultivatedhabitatwereorbweavers,makingup53%ofthetotalindividualsinthehabitat.Thesecondmostabundantguildwasthespacewebbuilders,makingup21%ofthetotalindividualsinthehabitat(figure8C).Themost
Ambush Hunter3% Ground Hunter
2%
Space Web53%
Orb Weaver9%
Other Hunters5%
Sensing Web1%
Sheet Web28%
Unknw1%
Secondary Habitat Guilds
Orb weaver53%
Space web21%
Sheet Web10%
Other Hunter10%
Ground Hunter5%
Ambush Hunter1% Unkwn
1%
Cultivated Habitat Guilds
Space web 35%
Orb weaver14%Other Hunter
13%
Ground Hunter7%
Sensing Web1%
Sheet web26%
Ambush Hunter3%
Unknwn1%
Primary Habitat Guilds
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abundantfamilyinthehabitatTetranathidaeisclassifiedundertheorbweaverguild,whilethefollowingmostabundantfamiliesTheridiidaeandAraneidaefallintothespacewebandorbweaverguilds,respectively(table1).Only3guildswerefoundinthecavetransects,withthespecialistandspacewebguildsmakingup99%ofguildactivity(figure9).Comparedtotheguildcompositionofthethreemaintransectsthecaveecosystempresentsahighlevelofecologicalstressresultinginonlyafewguildsbeingabletoadapttotheextremesubterraneanenvironment(Mammolaetal2017.)
Figure9.CaveGuildCompositiondisplayedinpercentagesoutofthetotalnumberofindividualsfound.Therichnessandevennessofguildsincreasedfromthecultivatedtotheprimaryhabitat.Habitatswithlessanthropogenicinterventionwereabletosupportahigherrangeofguilds,resultinginhighermeasuresofbiodiversity(table2).Guildswithmorespecializedhuntingtechniqueswerefoundtobemorerepresentedinmoreunalteredhabitattypes(Michalko2016,Cardosoetal2011).Habitatswithhigherecologicalpressure(Mammolaetal2017)orincreasedlevelsofdisruptionwillonlybeabletosupportsimplisticguildcompositions,asthesehabitatslimittheamountofresources,structureandrefugeneededtosupportcomplexguildactivity(Cardosoetal2011).
Space Web72%
Specialist27%
Sensing Web1%
Cave Habitat Guild Composition
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VegetationandLandUseImpactThetypeofvegetationineachhabitatcouldbeclassifiedinto9categories.The8guildscouldbearrangedintothetypesofvegetationtheywerefoundusingtohunt.
Figure10.Vegetationandstratapresentinthefourhabitats,withdesignationoftypeandtheguildsfoundusingtheinfrastructure.Vegetationvariabilitywasfoundtodecreaseacrossthefourhabitatssampled,parallelingadecreaseinthebiodiversityandactiveguildsinthehabitat.Boththeprimaryandsecondaryhabitatsshowedthehighestrangeinvegetationtype,whilethecultivatedhabitatshadonly4outofthe9classifications.Thecaveecosystemsshowednovegetationandonlyonestrataclassification(figure10).Thespeciesrichness,familyandguildpresencebetweenthemainthreetransectsandthecavesamplesshowedadramaticdecrease,withonly6morpho-species,4familiesand3guildsbeingfoundthroughoutthecavessurveyed(appendixA.)Astheecologicalstressorsincreased,classifiedindiminishingvegetationvariability,thediversityofthespiderpopulationsdecreasedproportionally(Mammolaetal2017).Theavailabilityanddiversityofvegetationdirectlyimpactedthebiodiversitypresentacrosstheregion.Asvegetationandstratacomplexityincreasedthenumberofactiveguildsincreased.Thiscontributestotheincreaseofbiodiversityasthesupportofmoreguildtypesleadstothepresenceofmorespecies(Cardosoetal2011).Asbothofthesecondaryandcultivatedhabitatshadbeenpreviouslyalteredandbothhadvaryingdegreesofdensevegetationtype,similarspecieswouldfindthemhospitable.Theywerealsoclosertogetherinlocation,meaningmorespecieshadtheabilitytocrossoverfromhabitattohabitat.Spidersinadaptiveguildssuchasspacewebororbweaverswillbeabletothriveinvaryinghabitattypes,asbothrelyonvegetationstructurebutcanadapttovaryingvegetationtobuildwebs(Schüpbach2003).Astheprimaryforestandthecultivatedfieldshadthegreatestdegreeofimpactdifference,itisexpectedtheywouldsharetheleastamountofmorpho-species(table3).
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Thesignificantdifferencebetweenanthropogenicimpactofunalteredprimaryforestandcultivatedfieldswouldsupportstheassumptionthatspeciesinprimaryforestwouldnotfindagriculturalareasashospitable(Uetz1991).Thecultivatedtransectshowevershowedarelativelyhighbiodiversitymeasure(table2).AsfoundbyMarc&Canard(1997)agriculturalzoneswithlittletonochemicalimpactwillbehospitabletoarangeofspidersandtheirrespectiveguilds.Theyalsofoundhigherspiderbiodiversityincultivationhasthepotentialtoactasaneffectivepestcontrol,andwiththeintersectionofarangeofguilds,cantargetinsectsinalloftheirlifestages.Thepercentageofbiodiversityfoundinthecultivatedtransectsrepresentacultivatedareawithgoodagroecologicalmanagement.Cultivatedlandthathasbeenabandonedtoacertaindegreewillalsopresenthigherlevelsofbiodiversity,asthelackofchemicaluseandconsistentdisturbancepermitsspiderpopulationstoincrease(Martin1982).ConclusionSpiderbiodiversityaroundtheworld,andspecificallytheneotropics,isstillabiologicalfrontiertobefullyunderstood(Basset2012).Presentinganewfrontierofnewscientificdiscoveries,spidersdisplayanintriguingrangeoftaxonomyandecologicalinteractionsthatrivalscomparativetop-levelpredatorsonothertrophiclevels(Basset2012,Silva1992).Thisstudyfoundspiderbiodiversitydecreasedwithincreasedanthropogenicimpact.Primaryforestswerefoundtosupportmorespiderfamiliesandprovideinfrastructureforincreasedguildactivity.Themostimpactedregions,thecultivatedhabitats,showedadecreaseindiversity,withafewspeciesdominatingtheecosystem.Theclassificationofvegetationtypeshowedthatadecreaseinvariabilitycorrespondedtoadecreaseinbiodiversity.Inboththecultivatedandcaveecosystems(imposingbothartificialandnaturalecologicalpressures)fewerfamiliesandguildscouldbesupported.Thisdemonstrateshowecologicallymindfullandmanagementisvitalinpreservingspiderbiodiversity,asincreasedecologicalpressurelessentheresourcesneededbythemorecomplexguilds.Theuniquebiodiversityfoundintheprimaryforestsshowedhowpreservationofpristineenvironmentsisvital,especiallyinthecaseofspiderswheremanyspecieshaveyettobedescribed(Platnick2013).Thecultivatedhabitatbiodiversitydidshowhowmindfulagriculturalpracticescanmaintaindiversespiderpopulations,simultaneouslycreatingeffectivepestcontrol(Jeanneretetal2003).Spiderbiodiversityacrosshabitatscallsforincreasedscientificexploration,asknowledgeofdiversityacrosstrophiclevelsisnecessarywhendevelopingcompleteconservationprotocols.BibliographyAvezedo,G.H.F,etal.(2014.)Effectivenessofsamplingmethodsandfurthersampling
foraccessingspiderdiversity:acasestudyinaBrazilianAtlanticrainforestfragment.InsectConservationandDiversity.7:381-391.doi:10.1111/icad.12061
Basset,Y.etal.(2012).ArthropodDiversityinaTropicalForest.Science,338(6113):1481-1484.DOI:10.1126/science.1226727
Brescovit,A.,Rheims,C.A.,Bonaldo,A.B.[nodate]ChavedeIdentificacionpara
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Cardoso,P.,Pekar,S.,Jocque,R.,&Coddington,J.A.(2011).Globalpatternsofguildcompositionandfunctionaldiversityofspiders.PLoSONE,6(6).https://doi.org/10.1371/journal.pone.0021710
Chao,A.,Ma,K.H.,andHsieh,T.C.(2016)iNEXT(iNterpolationandEXTrapolation)Online.ProgramandUser'sGuide.http://chao.stat.nthu.edu.tw/wordpress/software_download/
Coddington,J.A.,Hebert,L.W.(1991).SystematicsandEvolutionofSpiders(Araneae.)AnnualReviewofEcologyandSystematics.22:565-592.https://www.jstor.org/stable/2097274
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Duperre,N.,TapiaE.(2016.)OverviewoftheAnyphaenids(Araneae,Anyphaeninae,Anyphaenidae)spiderfaunafromtheChocoforestofEcuador,withthedescriptionofthirteennewspecies. EuropeanJournalofTaxonomy.255:1-50.http://dx.doi.org/10.5852/ejt.2016.255
Hall,D.(2019.)OrchardOrbweaver,OrchardSpider.IFASExtension,UniversityofFlorida.Vol2019(2).https://journals.flvc.org/edis/article/view/108777
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Robinson,K.(2018.)AraneaeBiodiversityintheEcuadorianChocó:ImpactofAltitudeandLandUseonSpiderDiversity.SITEcuador:ComparativeEcologyandConservation.
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AppendixA:Thenumberofmorpho-species,families,guildsandindividualsfoundineachhabitattype.Habitat Morpho-species Families Guilds Individuals
PrimaryForest
73
17
6
313
SecondaryForest
64
13 7 320
CultivatedFields
68 11 6 341
Caves 6 4 3 60
AppendixB:TheFamiliesandguildsfoundineachhabitattype.Habitat Families GuildsPrimary agelenidae AmbushHunter anyphaenidae GroundHunter araneidae Orbweaver corinnidae OtherHunter ctenidae SensingWeb deinopidae Sheetweb heteropodidae Spaceweb lycosidae Unknwn pholcidae pisauridae salticidae scytodidae symphytognathidae tetranathidae theraphosidae theridiidae thomisidae
Unknwn
Secondary Anyphaenindae AmbushHunter Araneidae GroundHunter Corinnidae OrbWeaver Ctenidae OtherHunters Lycosidae SensingWeb Pholcidae SheetWeb Pisauridae SpaceWeb Salticidae Unknwn Scytopidae Tetranathidae Theridiidae Therophosidae Thomisidae Unknwn
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Cultivated Araneidae AmbushHunter Corinnidae GroundHunter Ctenidae Orbweaver Deinopidae OtherHunter Dysderidae SheetWeb Lycosidae Spaceweb Pisauridae Unknwn Salticidae Tetranathidae Theridiidae Thomisidae
Unknwn
Caves Gnaphosidae Specialist Pholcidae SpaceWeb Theridiidae SensingWeb Theraphosidae AppendixC:RegionalDominanceCurveandFamilyPercentComposition
AppendixD:BiodiversityComparisonsHabitat Simpson Entropy Comparison Difference % increase
P 3.86 C/S 1.68 61.31% S 2.74 C/P 2.8 72.54% C 1.06 S/P 1.12 29.02% Habitat Gini-Simpson (transformed) Comparison Difference % increase P 25.58 C/S 11.47 67.23% S 17.06 C/P 19.99 78.15% C 5.59 S/P 8.52 33.31%
23.36%
18.24%
17.95%
9.65%7.63%
4.25%
2.51%2.22%
2.12% 1.35%0.97%
0.77%0.68%
0.58%0.58%
0.29%0.29%
0.29%0.19%
0.19%0.10%
0.00%
5.00%
10.00%
15.00%
20.00%
25.00%
Pholcidae
Therid
iidae
Tetra
nathidae
pisaurid
ae
Araneidae
Saltic
idae
Lycosid
ae
Ctenidae
Gnaphosid
ae
Thomisid
ae
Corinnidae
scytodidae
Heteropidae
Therap
hosidae
Unknwn
Agenele
nidae
Anyphae
nidae
Dysderid
ae
Deinopidae
symphyto
gnath
idae
Miturgi
dae
Regional Family Dominance Curve