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Using DNA barcoding and GenBank data for west Central African amphibian conservation PDF

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Preview Using DNA barcoding and GenBank data for west Central African amphibian conservation

RESEARCHARTICLE How many species and under what names? Using DNA barcoding and GenBank data for west Central African amphibian conservation JessicaL.Deichmann1*,DanielG.Mulcahy2,HadrienVanthomme1,ElieTobi1,Addison H.Wynn3,BredaM.Zimkus4,RoyW.McDiarmid5 a1111111111 1 CenterforConservationandSustainability,SmithsonianConservationBiologyInstitute,NationalZoological Park,Washington,DC,UnitedStatesofAmerica,2 GlobalGenomeInitiative,NationalMuseumofNatural a1111111111 History,SmithsonianInstitution,Washington,DC,UnitedStatesofAmerica,3 DepartmentofVertebrate a1111111111 Zoology,DivisionofAmphibiansandReptiles,NationalMuseumofNaturalHistory,SmithsonianInstitution, a1111111111 Washington,DC,UnitedStatesofAmerica,4 MuseumofComparativeZoology,HarvardUniversity, a1111111111 Cambridge,MA,UnitedStatesofAmerica,5 USGS,PatuxentWildlifeResearchCenter,NationalMuseumof NaturalHistory,WashingtonDC,UnitedStatesofAmerica *[email protected] OPENACCESS Abstract Citation:DeichmannJL,MulcahyDG,Vanthomme H,TobiE,WynnAH,ZimkusBM,etal.(2017)How DevelopmentprojectsinwestCentralAfricaareproceedingatanunprecedentedrate,often manyspeciesandunderwhatnames?UsingDNA barcodingandGenBankdataforwestCentral withlittleconcernfortheireffectsonbiodiversity.Inanattempttobetterunderstandpotential Africanamphibianconservation.PLoSONE12(11): impactsofaroaddevelopmentprojectontheanuranamphibiancommunity,weconducted e0187283.https://doi.org/10.1371/journal. abiodiversityassessmentemployingmultiplemethodologies(visualencountertransects, pone.0187283 auditorysurveys,leaflitterplotsandpitfalltraps)toinventoryspeciespriortoconstructionof Editor:StefanLo¨tters,UniversitatTrier,GERMANY anewroadwithinthebufferzoneofMoukalaba-DoudouNationalPark,Gabon.Becauseof Received:November15,2016 difficultiesinmorphologicalidentificationandtaxonomicuncertaintyofamphibianspecies Accepted:September6,2017 observedinthearea,weintegratedaDNAbarcodinganalysisintotheprojecttoimprove theoverallqualityandaccuracyofthespeciesinventory.Basedonmorphologyalone,48 Published:November13,2017 specieswererecognizedinthefieldandvoucherspecimensofeachwerecollected.We Copyright:Thisisanopenaccessarticle,freeofall usedtissuesamplesfromspecimenscollectedatourfieldsite,materialavailablefrom copyright,andmaybefreelyreproduced, distributed,transmitted,modified,builtupon,or amphibianscollectedinotherpartsofGabonandtheRepublicofCongotoinitiateaDNA otherwiseusedbyanyoneforanylawfulpurpose. barcodelibraryforwestCentralAfricanamphibians.Wethencomparedoursequenceswith TheworkismadeavailableundertheCreative materialinGenBankforthegenerarecordedatthestudysitetoassistinidentifications.The CommonsCC0publicdomaindedication. resultingCOIand16Sbarcodelibraryallowedustoupdatethenumberofspeciesdocu- DataAvailabilityStatement:16SandCOI mentedatthestudysiteto28,therebyprovidingamoreaccurateassessmentofdiversity sequenceshavebeendepositedinGenBankunder anddistributions.WecautionthatbecausesequencedatamaintainedinGenBankareoften theaccessionnumbersKY079387-KY080438.All COIand16Srecordshavealsobeendepositedin poorlycuratedbytheoriginalsubmittersandcannotbeamendedbythird-parties,these BOLD(ProcessIDs:WAFRA001-14toWAFRA542- datahavelimitedutilityforidentificationpurposes.Nevertheless,theuseofDNAbarcoding 14;WestCentralAfricanamphibianbarcodelibrary islikelytobenefitbiodiversityinventoriesandlong-termmonitoring,particularlyfortaxathat forbiodiversity). canbedifficulttoidentifybasedonmorphologyalone;likewise,inventoryandmonitoring Funding:ShellGabonfundedthefieldworkinthe programscancontributeinvaluabledatatotheDNAbarcodelibraryandthetaxonomy LMRstudyarea.TheSmithsonianInstitution’s ofcomplexgroups.Ourmethodsprovideanexampleofhownon-taxonomistsand DNABarcodeNetworkprovidedfundingforall laboratorywork.Thefundershadnoroleinstudy PLOSONE|https://doi.org/10.1371/journal.pone.0187283 November13,2017 1/38 DNAbarcodingforAfricanamphibianconservation design,datacollectionandanalysis,decisionto parataxonomistsworkinginunderstudiedpartsoftheworldwithlimitedgeographicsam- publish,orpreparationofthemanuscript.The plingandcomparativemorphologicalmaterialcanuseDNAbarcodingandpubliclyavailable SmithsonianConservationBiologyInstituteandthe sequencedata(GenBank)torapidlyidentifythenumberofspeciesandassigntentative NationalMuseumofNaturalHistory’sLaboratories ofAnalyticalBiologyprovidedin-kindsupport. namestoaidinurgentconservationmanagementactionsandcontributetotaxonomic resolution. Competinginterests:Whilethefieldwork presentedinthispaperwasfundedbyShellGabon (listedinthefinancialdisclosuresection), representingprivatesectorfunds,theSmithsonian Institutionmaintainsallintellectualpropertyand rightsindata,andwedeclarenocompeting interestsexist. Introduction Specieslistsarenecessaryforconservationplanningandmanagement[1].Assuch,conserva- tionbiologistsandecologistsmustprovidetaxonomicinformationtodecision-makersfor conservationeffortstomoveforward.Unfortunately,taxonomyhasnotkeptpacewithhabitat lossinhighbiodiversityareas[2],andacommoncriticismofstudiesinconservationbiology andecologyarethattheylacktaxonomicrigor[2,3].Putsimply,thereisanurgentneedfor taxonomicnamesandcountsofspecies,butassigningdefinitivenamesanddistinguishing closelyrelatedspeciesisproblematic,moresoforsomegroupsthanothers. InCentralAfrica,asinmanyotherpartsoftheworld,economicdevelopmentisputting increasedpressureonbiodiversity[4].Expansionoflogging[5],roaddevelopment[6],agri- culture[7],oilandgasdevelopment[8],andotherformsofenergydevelopmentarecausing changesinlandusepatternsandconsequentlyaffectingbioticcommunities.Spendingon infrastructureinAfricabetween1998and2007increasedannuallyby17percentandthat growthisexpectedtoaccelerate[9].Itisestimatedthatupto$450billionwillbeinvestedin energyinfrastructuredevelopmentandproductioninsub-SaharanAfricaoverthenextfew decades[10].Consequently,EnvironmentalImpactAssessments(EIAs)areroutinelybeing carriedoutinmanyAfricannationstoevaluatepotentialeffectsofvariousproposeddevelop- mentprojectsontheenvironment. Expectedchangesinlandusecombinedwithprojectedclimatechangearelikelytohave particularlynegativeconsequencesfortropicalAfricanamphibianbiodiversity[11].Amphibi- ansplayacrucialroleinproperlyfunctioningecosystems,contributingtonutrientcycling, bioturbation,energyflow,foodwebs,andotherecosystemdynamics[12,13].Theseanimals provideadditionalecosystemservicesvaluabletohumans,suchasregulatingpests,actingasa foodsource,functioningasmodelsformedicalresearchandservingassubjectsofrecreational andspiritualimportancethatvaryacrosscultures[13,14].Giventheircriticalimportancein functionalecosystems,maintenanceofamphibiandiversityinthefaceofanthropogenic changeisessential.However,inordertobeabletomaintainamphibiandiversity,wemust firstaccuratelymeasureitsothatchangescanbedocumentedandrestorationmeasuresimple- mentedindisturbedsystems. Unfortunately,theissueofdeterminingthetotalnumberofspeciesofamphibiansina givenareaisnotasimpletask.Inspiteofthefactthatamphibiansarethemostthreatened groupofvertebratestobeassessedtodate[15,16],speciesofthisclassarealsoamongthe mostpoorlyknownvertebrategroupsinmanygeographicareas(e.g.[17]).IntheAfrotropics inparticular,thelackofbasicknowledgeregardingamphibianspeciestaxonomyandrichness andhighnumbersofundescribedspeciesmakethetaskofsurveyingandidentifyingamphibi- ansmoredifficult[18].Althoughrecenttaxonomicfieldguideshaveimproved(e.g.[19]), anuransincludegroupsrifewithcrypticspecies[20],andotherswithhighlevelsofintraspe- cificphenotypicpolymorphismexist[21,22].Thesefactorscomplicatenotonlyspecimen identification,butalsosimpledocumentationofthenumberofspeciesatagivensite. PLOSONE|https://doi.org/10.1371/journal.pone.0187283 November13,2017 2/38 DNAbarcodingforAfricanamphibianconservation Confoundingmattersevenfurther,expertiseinamphibiantaxonomyislimitedgloballyand tendstoberestrictedtocountrieswithhigheconomicincome[23].Inmanycases,basicbiodi- versityassessmentsindevelopingcountriesarecarriedoutbyparataxonomists,invaluable fieldpersonnelchargedwithsortingspecimensintotaxonomicunits,whovaryintrainingand abilitytoevaluatediagnosticmorphologicaltraits[24–27].Makingmattersworse,published keysmeanttoaideinidentificationcanbeunclear,confusing,orinneedofimprovement becausemanyproblematicgroupshavenotbeenworkedouttaxonomically. Integratingadditionaltoolsintotraditionalmorphologicalspeciesinventoriescancontrib- uteagreatdealtotheaccuracyandprecisionofspeciesrichnessestimatesinanarea[28–30]. DNAbarcodingisonesuchtoolthatcanbeaddedatrelativelylimitedcostsandpresentsnon- taxonomistswithawaytoverifyandimproveidentificationsandspeciesdiversityestimates [31–33].DNAbarcodingislikelytobeaveryusefultoolinspeciesmonitoring,particularlyfor taxathatcanbedifficulttodistinguishbasedonmorphologyalone(i.e.crypticspecies).In addition,DNAbarcodingcanalsoreduceerrorsinidentifyingspecieswithhighphenotypic variabilityandpolymorphisms,whichislessfrequentlydiscussedintheliteraturewhencom- paredtoitspotentialtoaidincrypticspeciesidentification. TheadventofDNAbarcodinghasopenedupnewpotentialsolutionstotheissueofcharac- terizingdiversity;however,thismethodrequirescarefulinterpretationwhenusedtoassign namestogroupsofsimilarspecimens(i.e.clustersoroperationaltaxonomicunits[OTU]) [34],particularlywithamphibians[35].WhenaDNAbarcodelibraryexistsforcomparisons ofspecimensfromthefield,itcanbeusedtoidentifyspecimenstoaspecies[36].Infact,the existenceofDNAbarcodelibrarieshasprovenusefulforavarietyofbiodiversityassessments (e.g.[32,33,37,38])andecologicalstudies[39,40]representingdifferenttaxonomicgroups. However,giventhattheintentofDNAbarcodingisnottoreconstructtheevolutionaryhistory ofalineage[36],theusefulnessofaDNAbarcodelibraryforassigningnamestoOTUsis heavilydependentontheaccuracyofreferencesequences.Misidentifiedandconsequently mislabeledspecimensandtheirassociatedsequencedatacanhindertheabilitytoidentify specimensaccurately. Herewereporttheresultsofanintegratedamphibiansurveyinanareainsouthwestern Gabonpriortotheconstructionofaroad.Ourprimarygoalwastodocumentamphibianspe- ciesrichnesswithinthestudyareasothatappropriateconservationmanagementmeasures couldbetakenduringandafterdevelopment.WeusetheresultsofourDNAbarcodinganaly- sestoidentifyspecimens,therebyrefiningourinitialfieldidentificationsbasedonmorphol- ogy,followedbysystematiccomparisonsofourgeneticmaterialtosequencesinGenBank, morphologicalcomparisonstoadditionalmaterialsavailableintheNationalMuseumofNatu- ralHistory(NMNH),andtheprimaryliterature,includingrecentworkandoriginalspecies descriptions.Bydoingso,wecontributemorewidelytoaDNAbarcodelibraryforamphibians ofthisregionandsummarizethecurrentknowledgeofwestCentralAfricananurantaxonomy byincludinggeneticmaterialofspecimensavailabletousattheNMNH. Wepresentthisasamodelstudyforusebyparataxonomists,ecologistsandconservation biologistsneedingtorapidlydefinetaxonomyofproblematicgroupsusingDNAbarcoding andlimitedcomparativematerial.Ourstudydemonstrateshowadditionaltaxonomicexper- tiseandcomparativematerialcanbeusedforproblematicgroups.Inparallel,weofferadvice totaxonomistswhohavemorecomparativematerialandadditionalresourcesavailableto undertakefuturecomprehensivetaxonomictreatmentsofthesegroups.Throughthiswest CentralAfricancasestudy,weprovidemethodologicalinsightsthat,ifimplemented,will betterintegratebiodiversityinventoriesandtaxonomyforthebenefitofbiodiversity conservation. PLOSONE|https://doi.org/10.1371/journal.pone.0187283 November13,2017 3/38 DNAbarcodingforAfricanamphibianconservation Materialsandmethods Studyarea ThestudysiteliesalongtheAtlanticcoastofGabonintheNyangaProvinceandincludesa mosaicofgrassland,secondaryforests,andwetlandscoveringapproximately175km2(Fig1). Annualrainfallaveragesroughly2,000mm.AshortdryseasonoccursinJanuarywithalonger dryseasonfromlateMaytoSeptember.Theresearchareaisa52km-longbandcenteredon theprojectedpathoftheLoubomo-MougagaraRoad(LMR)andextending2–3kmoneither side.Moukalaba-DoudouNationalParkbordersmostoftheresearchareatothenortheast, andtheeasternendoftheLMRpathterminatesattheN6road.Theareaisborderedtothe southandwestbytheAtlanticOcean.In2014(afterbiodiversitysurveys),constructionofthe two-laneLMRbeganandthelateritephaseoftheroadwascompletedin2016. Fieldsampling WesampledamphibiansbetweenMay20–June19,2012(earlydryseason)andMarch13– April23,2013(shortwetseason2013).Weusedavarietyofsamplingmethods,includingnoc- turnalanddiurnalvisualandacousticsurveysalong22pre-determinedandrandomlyselected 500mtransectsinallhabitattypes(forests,savannas,swampmargins),pitfalltrapsnearhabi- tattransitionzones,andopportunisticvisualencounters. Inthedryseason,theresearchteamconsistedofaparataxonomist(ET)previouslytrained inamphibiantaxonomy,astudent,andafieldassistant.Inthewetseason,theteamwasjoined byalabassistantandamoreexperiencedamphibianbiologist(JLD),albeitanoviceinAfrican amphibiantaxonomy.Weusedpublishedassessmentsandspecieslistsofamphibiansof Gabon[41–43]andafieldguide[19]toidentifyspecimensinthefield.Voucherswerecol- lectedforallmorphologicallyrecognizedspecies(morphospecies),andsomewerealsophoto- graphed.Specimenswereeuthanizedinthefieldusing20%benzocainegel(Oragel)appliedto theventralsurfaceofthebody[44].Aftereuthanasia,asampleofthighmusclewastakenand Fig1.Loubomo-MougagaraRoad(LMR)studyareaforamphibianbiodiversityinventoryinNyanga province,Gabon. https://doi.org/10.1371/journal.pone.0187283.g001 PLOSONE|https://doi.org/10.1371/journal.pone.0187283 November13,2017 4/38 DNAbarcodingforAfricanamphibianconservation thetissuestoredin95%ethanol.Voucherspecimensweresubsequentlypreservedin10%for- malinandstoredin70%ethanol.SpecimensweredepositedinthecollectionoftheUnited StatesNationalMuseum(USNM)housedattheNMNH,SmithsonianInstitution,Washing- ton,DC.Inordertoconfirmspeciesidentificationsmadeinthefield,webarcoded80speci- mensfromthefirst(dry)seasonand97specimensfromthesecond(wet)samplingseasonfor atotalof177specimensfromtheLMRstudyarea. Ethicsstatement LMRspecimenswerecollectedunderresearchpermitsAR0016/12,AR0004/13and 00170MEFfromtheCentreNationaldelaRechercheScientifiqueetTechnologique,the AgenceNationaledesParcsNationaux,andtheDirectiondel’Ame´nagementdesAiresProte´- ge´esofGabon.TheLMRfieldstudywascarriedoutinstrictaccordancewiththeguidelines setforthbytheAmericanSocietyofIchthyologistsandHerpetologists(ASIH),theHerpetolo- gists’League(HL),andSocietyfortheStudyofAmphibiansandReptiles(SSAR).TheLMR specimeneuthanasiamethodhasbeenapprovedbytheaboveinstitutionsaswellastheAmeri- canVeterinaryMedicalAssociation[44],andalleffortsweremadetominimizesuffering.The protocolwasapprovedbytheSmithsonianNationalZoologicalPark’sInstitutionalAnimal CareandUseCommittee(NZP-IACUCpermit#12–13). DNAbarcodeprotocol ExtractionsofgenomicDNAwereperformedonanAutoGenprep965(2011AutoGen,Inc.), usingthemanufacturer’sstandardphenolprotocol.GenomicDNAwaselutedin100μlof AutoGenR9re–suspensionbuffer.Polymerasechainreactions(PCR)wereconductedforthe mtDNAlargeribosomalsubunit(rrnL:16S)andcytochromeoxidasesubunitI(COI)using theprimers:16Sar5' CGCCTGTTTATCAAAAACAT 3'and16Sbr5' CCGGTCTGAACTCA GATCACGT 3'[45]andCOI–fishCO1F5' TCAACYAATCAYAAAGATATYGGCAC 3'and fishCO1R5' ACTTCYGGGTGRCCRAARAATCA 3'[46]orChmf45' TYTCWACWAAYCAY AAAGAYATCGG 3'andChmr45' ACYTCRGGRTGRCCRAARAATCA 3'[47].PCRcondi- tionswereperformedin10μlreactionsfollowingthe3.6PCRMethods:Amplificationprotocol ofWeigtetal.[48]withannealingtemperaturesof54˚Cfor16Sand48˚CforCOI.Sequence reactionswereperformedinbothdirectionswiththePCRprimersusingBigDye1Terminator v3.1CycleSequencingKit’sin0.25x10μlreactionsandrunonanAutomatedABI3730Se- quencer(2011LifeTechnologies).RawchromatogramswereeditedinSequencher1v5.1 (2012GeneCodesCorp.),complementarystrandswerealigned,andCOIwasinspectedfor propertranslation,usingtheDNAbarcodetrimcriteriadescribedinWeigtetal.[48].Align- mentsforbothgeneswereconductedusingtheMAFFTplug-ininGeneiousv8.1.7with defaultsettings.Wechosetocharacterizeaportionofthe16Sgeneinadditiontoproducing COIbarcodesforourspecimensbecauseweanticipatedneedingtocompareourdatatothe largeamountof16SsequencedataavailableinGenBankforwestCentralAfricananurans. Additionalreferencematerial InordertoaidinidentificationofspeciesfromtheLMRstudysite,webarcodedadditionalref- erencespecimensfromtheUSNMcollection.Weattemptedtosampleallspeciesknownto occurinGabon,aswellassomemuseumspecimenscollectedinneighboringRepublicof Congo(RC),forbarcodeanalyses(Fig2).InadditiontothematerialcollectedfromtheLMR studysite,webarcoded90specimenscollectedpreviouslyfromsitesinEstuaireandOgooue- MaritimeprovincesinGabon(approximately400and25kmfromtheLMRsite,respectively), and275amphibianspecimenscollectedfromfoursitesintheRC(Fig2).Allmaterialis PLOSONE|https://doi.org/10.1371/journal.pone.0187283 November13,2017 5/38 DNAbarcodingforAfricanamphibianconservation Fig2.Referencemapshowinglocalitiesofallbarcodedmaterial.Whitecircle:Estuaireprovince(Gabon), whitesquares:Ogooue-Maritimeprovince(Gabon),whitetriangles:Nyangaprovince(Gabon;LMRstudysite), blackcircles:Lekoumoudepartment(RepublicofCongo,RC),blacksquares:Likoualadepartment(RC),and blacktriangles:Pooldepartment(RC). https://doi.org/10.1371/journal.pone.0187283.g002 catalogedandhousedintheUSNMcollection.Tissuesfromthesespecimenswereinitially placedin95%ethanolandsubsequentlystoredat-80˚CafterdepositionintheUSNMcollec- tion.Somevoucherspecimens,includingthosefromtheLMRsite(N=2),otherGabonese sites(N=3),andCongolesesites(N=7),havebeenlostordestroyed.Forsomeofthosespeci- mens,photographsserveasthevoucherandarereferredtoasUSNMHerpImageNumber (N=3);theothertissuesampleswithoutphotographicvouchersarecataloguedasUSNM HerpTissueNumber(N=9). Inadditiontousingavailablemuseumspecimens,wealsoqueriedtheBarcodeofLifeData- base(BOLD)andGenBankforsequencesfromallamphibianspeciesknowntooccurin region(asof11November2016)andforallgeneraforwhichwegeneratedsequencedatafor comparativepurposes. Dataanalysis ResearchersuseavarietyofmethodsforanalyzingDNAbarcodedata,includingpercent sequencedivergence[49],neighbor-joining(NJ)trees[36],theBarcodeIndexNumber(BIN) PLOSONE|https://doi.org/10.1371/journal.pone.0187283 November13,2017 6/38 DNAbarcodingforAfricanamphibianconservation System[50],andhaplotypenetworks[51]amongothermethods.Givenourleveloftaxonomic andgeographicsampling,wechoseavarietyofmethodstoanalyzeourdataincludingpercent sequencedivergence,neighbor-joiningtrees,BINs,andtheAutomaticBarcodeGapDiscovery (ABGD)method[52]. ForCOIdata,wefirstusedtheBarcodeIndexNumber(BIN)System[50]generatedin BOLDforspecimenidentification.However,becausetheavailableDNAbarcodelibraryfor anuransislimited,wecouldnotrelysolelyonthismethod.Forexample,asearchinGenBank (Dec.2015)for‘Anura’and‘Africa’reveals170COIrecords(120ofwhichwerefromfrogsof thegenusXenopus).InadditiontotheBINsmethod,weincorporatedanalternativeassess- mentofspecimenidentificationusingtheAutomaticBarcodeGapDiscovery(ABGD)method [52]withourCOIdata.TheABGDmethodusesadjustableparametersforgroupsequences (weusedPmin-0.001,Pmax=0.1,10steps,X=1.5,andNb=20),ratherthanafixeddiffer- ence(e.g.>2.2%;BIN).Wedirectlycomparedtheresultsofthesetwomethods,whereasothers discusstheirdifferencesinmoredetail[52].WealsogeneratedNeighbor–joining(NJ)treesin PAUP(cid:3)v4.0b10[53]forthe16SandCOIdataseparately,andthetwolociwereconcatenated forallthesequenceswegeneratedinacombinedMaximumLikelihoodanalysisusingRAxML [54]andtheGTRGAMMAmodel(partitionedbygene)withsimultaneousfastbootstrap method(100replicates)andbestMLtreesearch.Wethenconductedneighbor-joiningtree searchesinPAUP(cid:3)withtheGenBank16Smaterialtoassesssequencesimilarity(seebelow). WeacknowledgethatNJtreesarenotidealforreconstructingevolutionaryhistory,particu- larlywiththesmallsizedDNAsequencesofCOIor16S.However,weusethemasausefultool forclusteringsimilarsequencesofputativemembersofthesamespecies,notforestimating evolutionaryrelationships.Wedidnotusehaplotypenetworksbecausetheyworkbestwhen taxonomicandgeographicsamplingaremostcomplete,whichisnotthecaseinourstudy. Mostofourspecimensperspeciesarefromeffectivelyonlyoneortwolocalitieswhereasthe specieslikelyoccurallthroughouttheregion. Taxonomicassignments Weattemptedtoassigneachspecimentoaputativespeciesgiventheresultsofvariouslinesof evidence(seebelow).Ifspeciesassignmentwasnotpossible,weassignedatemporaryspecies name(e.g.sp.A)toagivenspecimenorgroupsofspecimensthatwethinkrepresentthesame undescribedspecies,i.e.“knownunknowns”[36].Weconsiderthisaprocessof“speciesdis- covery”[36],wereconservativeinourassignmentsofspecimenstothesecategories,andwefol- lowedthegenerallineageconceptofspecies[55]usingthecriteriadefinedbelow. AsaresultofapaucityofexistingrecordsofanuranCOIbarcodesinBOLD,wewere unabletorelysolelyontheBINsmethodtoverifyidentificationsofourspecimens;therefore, wedeterminedthenumberofspeciesrepresentedbyourspecimensandtheirtaxonomybased onmultiplelinesofevidence:1)COIBINscalculatedinBOLDandtheABGDmethod;2)16S sequencescomparedwithGenBankmaterial;3)traditionalmorphologicalspeciesdescrip- tions,includingcomparisonstotypedescriptions,assessmentsofproximitytotypelocalities, andknowngeographicdistributionsoftheputativespeciesinquestion(forfurtherinforma- tion,seebelow). COIBINs. IfspecimenswereplacedinthesameCOIBINinBOLDandinasingle ABGDgroup,theywereconsideredthesamespecies.Ifspecimensinitiallyidentifiedasthe samespecieswereplacedinseparateBINsorABGDgroups,theywerefurtherevaluated.We directlycomparedtheresultsoftheABGDmethodwiththeBINs.IftheseparateBINsor ABGDgroupsincludedspecimensfromdifferentgeographiclocations,andthe16Sdata placedtheminthesameclade,theyweretreatedasthesamespecieswithgeneticvariation PLOSONE|https://doi.org/10.1371/journal.pone.0187283 November13,2017 7/38 DNAbarcodingforAfricanamphibianconservation assumedtobebasedongeography.Ifspecimensfromthesamelocalitywereplacedinseparate BINsorABGDgroupsandthe16Sdataplacedtheminthesameclade,theyweretreatedas thesamespecieswithpopulation-levelgeneticvariation.Ifspecimensfromthesamelocality wereplacedinseparateBINsorABGDgroupsandthe16Sdataplacedthemindifferent clades,theyweretreatedasseparatespecies. 16Ssequences. ForthesesamplesweusedcriteriasimilartoourCOIBINsandABGD groupsmethoddescribedabove,andtreated16ScladessimilartoCOIBINsandABGD groups.Wealignedallofthe16SsequencesfromGenBankwithoursequencesusingMAFFT inGeneious(defaultsettings),andgeneratedNJtreesinPAUP(cid:3).Specimensidentifiedasthe samespeciesandinthesameclade,includingoursequencesandthosefromGenBank,were treatedasthesamespecies.Specimensidentifiedasthesamespeciesbutindifferentclades anddifferentlocalitiesbutmonophyletic(i.e.sistertoeachother)weretreatedasgeographic variationofthesamespeciesiftheyfitthemorphologicaldescriptionofthatspecies(see below).Iftheydidnotfitthemorphologicaldescriptionofthatspeciesorshowedsubstantial geneticvariation,theyweretreatedasdifferentspecies.Specimensmorphologicallyidentified asthesamespeciesbutindifferentclades,sistertootherspeciesweretreatedasdifferent species. Morphologicalspeciesdescriptions. Giventhetaxonomicscopeofourproject,thetime- linessoftheprojectinconjunctionwithspecimenscurrentlyonloantootherresearchers,and thefactthatmanyGenBankvoucherspecimensaredifficulttotrackdown,wereunableto examinethemorphologyofallGenBankvouchers.Itislikelythatparataxonomistsworkingin developingcountrieswouldalsohavedifficultyinsuchanundertaking.Therefore,weoffer thismorerapidcursurymethodasanintermittentsolutiontothetaskofproperamphibian taxonomy.Additionally,wecouldnotrelyentirelyonspeciesidentificationsinGenBank,we realizedinconsistentandinaccurateidentificationscouldaffectallspecimens(fromtheLMR studysite,referencematerial,andotherGenBanksequences).Accordingly,weattemptedto verifytheidentityoftheLMRsitespecimensbycomparingthemtomorphologicaldescrip- tionsofspecies,includingoriginaldescriptionsandsubsequentworks,andtakingintoaccount thegeographicdistancebetweenourspecimensandtheGenBankrecords,aswellasthe geneticdistancesbetweensequences.Unfortunately,nomethodoralgorithmtakesallofthese factorsintoaccounttodeterminespeciesdesignationsautomatically.Therefore,wereliedon ourtaxonomicexpertiseregardinganurandiversityinthisregion.Insodoing,weattempted tobeconservative,recognizingwidespread,geneticallyvariablespecies(ratherthanidentifying eachgeographiccladeasadistinctspecies),andpointoutcaseswhereadditionalsampling, datacollection,andanalysesareneededtoinvestigatefurtherwhatmayrepresentgreater diversitythanpreviouslyrecognizedinsuchgroups. Weacknowledgethatthismethodisoverlysimplistic,andtruespeciesboundariesmaybe maskedbyfactorssuchashybridization,incompletelineagesorting,andgeographicstructure inconsistentwithtaxonomy.However,weproposethisasamethodforparataxonomistswork- ingindevelopingcountriestoobtainaccuratespeciesinventories,whichmayalsobridgecon- servationecologistsandtaxonomistsinfurthersortingoutwestCentralAfricanamphibian taxonomythroughsupplementedgeographicandtaxonomiccoverage(demonstratedon amphibianshere,butmayalsobeappliedtoothertaxonomicgroups). Communityspeciesrichnessanalysis Usingtheresultsoffield(in-situandmorphologically-based)identificationsandofDNAbar- codeidentificationsofamphibianspecimenscollectedintheLMRstudyareaduringeachsam- plingperiod(dryandwetseasons)andoverall,weemployedEstimateS[Version9.1,56]to PLOSONE|https://doi.org/10.1371/journal.pone.0187283 November13,2017 8/38 DNAbarcodingforAfricanamphibianconservation calculatesample-basedrarefactioncurvesforspeciesrichnessandtocalculatethenon- parametricincidence-basedspeciesrichnessestimator,Chao2[57]foreachidentification methodandineachseason.Weusedsample-basedratherthanindividual-basedrarefaction becausereferencematerialwasnotcollectedforallindividualsencounteredinthefield;there- fore,anyabundance-orindividual-basedrichnessestimateswouldbeinaccurate.Richness estimatesfortheLMRstudysitepresentedherearebasedsolelyondatafromcollectedmate- rial.Todeterminestatisticalsignificanceofrarefiedspeciesrichness,wecomparedoverlapof 84%(P=0.05)confidenceintervalsoftheaccumulationcurvesforeachseason[58,59]. Results Moleculardata WecharacterizedDNAsequencedatafrom540specimens,including524COIDNAbarcode sequencesrangingfrom498–654base-pairs(bp)obtainedandplacedin94BINsinBOLDand 85ABGDgroups,and52816Ssequencesrangingfrom493–579bp(Table1).Ourmaterial includedonecaecilianspecimen(Gymnophiona)and539specimensfrom12families,21gen- era,and72speciesofanurans.OurconcatenatedalignmentofCOIsequenceswas654bp,and the16Salignmentwas655bp.Our16SandCOIsequenceshavebeendepositedinGenBank undertheaccessionnumbersKY079387–KY080438,andweincludedtracefilestoobtainthe Keyword"Barcode"inGenBankforallCOIsequences.AllCOIand16Srecordshavealso beendepositedinBOLD(ProcessIDs:WAFRA001-14toWAFRA542-14;WestCentralAfri- canamphibianbarcodelibraryforbiodiversity).Ourconcatenated(COIand16S)maximum- likelihoodphylogenyoftheDNAbarcodedspecimensshowsfamiliesobservedatourstudy siteandadditionalfamiliessampledinourreferencematerialfromelsewhereinGabonand theRC(Fig3).AlistofspeciesidentifiedattheLMRstudysite,elsewhereinGabon,andfrom theRCisshowninTable2alongwithadirectcomparisonofBINsandABGDgroups.Alldis- crepanciesbetweentheBINsandABGDgroupsarerestrictedtoinstanceswhereasinglespe- ciesconsistedofmultipleBINs.Specieswereplacedinto2–3BINs,butonlyinoneABGD groupinsevencases;twooftheseoccurredwheretherewere3BINsperspecies(Hyperolius olivaceusandH.adspersus).Inonecase,PhyrnobatrachusaurituswasplacedinthreeBINsand twoABGDgroups.ThesecasesresolvethedifferencebetweenthenumberofBINsandABGD groups.Interestingly,eightcasesoccurredwherespeciesputintomultipleBINswereequally dividedamongABGDgroups(Table2).Inallothercases,thetwomethodsagreed.Belowwe presentspeciesaccountsforspecimensidentifiedinourstudy,organizedtaxonomicallyby orderandfamily.TheassociatedNJtreescanbefoundinSupportingInformation(S1–S9 Figs).WediscussrelevantGenBanksequencesthatarepotentiallymisidentified. Table1. NumberofsampledspecimensandCOIand16Ssequencessuccessfullyamplifiedfromspecimensateachcollectionsite. CollectionLocality TotalNumberofSpecimens NumberofCOISequences Numberof16SSequences LMRstudysite(Season1) 79 79 79 LMRstudysite(Season2) 97 93 95 Gabon(Estuaire) 33 31 33 Gabon(Ogooue-Maritime) 57 56 57 RepublicofCongo(Kouilou) 7 7 7 RepublicofCongo(Lekoumou) 123 117 116 RepublicofCongo(Likouala) 73 72 70 RepublicofCongo(Pool) 71 69 71 TOTAL 540 524 528 https://doi.org/10.1371/journal.pone.0187283.t001 PLOSONE|https://doi.org/10.1371/journal.pone.0187283 November13,2017 9/38 DNAbarcodingforAfricanamphibianconservation Dermophiidae Geotrypetesseraphini(Dume´ril,1859). Wesequencedonespecimen(USNM576262) fromMayongongo,RC.The16Ssequenceisa99%matchtoaG.seraphinispecimencollected inGabon(FMNH256782),usedinbothFrostetal.(DQ283337[60])andRoelantsandBos- suyt(AY523754[61]).Our16Ssequenceis97%similartoaG.seraphinispecimen(BMNH 2005.2)fromCameroon[62].ThoughourCOIsequencewas94%similartotheBMNHspeci- men,itwasplacedinaseparateCOIBINandABDGgroup. Arthroleptidae(S1Fig) Arthroleptis. SixspeciesofArthroleptisareknowntooccurinGabon[42,63–65], although10differentmorphospecieswereidentifiedduringfieldworkattheLMRsite.Seven Fig3.Maximum-likelihoodphylogenyofthecombined16SandCOIDNAbarcodedataforallspecimenssequencedforthis study.Familycladesobservedatourstudysitearecolor-codedandshowarepresentativeimage.Thefourfamiliesshowningrey (includingthecaecilian)werenotobservedattheLoubomo-MougagaraRoadstudysitebutwereincludedasreferencematerialfrom othersitesinGabonortheRepublicofCongo. https://doi.org/10.1371/journal.pone.0187283.g003 PLOSONE|https://doi.org/10.1371/journal.pone.0187283 November13,2017 10/38

Description:
ment of specimen identification using the Automatic Barcode Gap Discovery (ABGD) method. [52] with our COI ABGD groups included specimens from different geographic locations, and the 16S data placed them in the .. The type locality for A. sylvaticus is ‴Buta', Uele, Dem. Rep. of Congo" [63].
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