DNA Barcoding reveals targeted fisheries for
endangered sharks in Indonesia
ARTICLE
in
FISHERIES RESEARCH · APRIL 2015
Impact Factor: 1.9 · DOI: 10.1016/j.fishres.2014.11.003
CITATIONS
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READS
302
13 AUTHORS
, INCLUDING:
Dian Pertiwi
Indonesian Biodiversity Research Center
1
PUBLICATION2
CITATIONSSEE PROFILE
Rizki Wulandari
San Diego State University
2
PUBLICATIONS2
CITATIONSSEE PROFILE
Dita Cahyani
Indonesian Biodiversity Research Center
6
PUBLICATIONS7
CITATIONSSEE PROFILE
Gusti Ngurah Mahardika
Udayana University
42
PUBLICATIONS110
CITATIONSSEE PROFILE
ContentslistsavailableatScienceDirect
Fisheries
Research
jo u r n al h om ep ag e :w w w . e l s e v i e r . c o m / l o c a t e / f i s h r e s
Short
Communication
DNA
barcoding
reveals
targeted
fisheries
for
endangered
sharks
in
Indonesia
Andrianus
Sembiring
a,g,
Ni
Putu
Dian
Pertiwi
a,
Angka
Mahardini
a,
Rizki
Wulandari
a,
Eka
Maya
Kurniasih
b,
Andri
Wahyu
Kuncoro
c,
N.K.
Dita
Cahyani
a,
Aji
Wahyu
Anggoro
a,
Maria
Ulfa
d,
Hawis
Madduppa
b,
Kent
E.
Carpenter
e,
Paul
H.
Barber
f,
Gusti
Ngurah
Mahardika
a,∗aTheIndonesianBiodiversityResearchCentre,TheAnimalBiomedicalandMolecularBiologyLaboratoryofUdayanaUniversity,JlSesetan-Markisa6, Denpasar,Bali,Indonesia
bFacultyofFisheriesandMarineScience,BogorAgriculturalUniversity,JlRasamala,Bogor,WestJava,Indonesia
cMarineScienceDepartment,FacultyofHusbandry,Fisheries,andMarineScience,UniversityStateofPapua,JalanGunungSaljuAmban,Manokwari, Papua,Indonesia
dFloraandFaunaInternational,JlCumi-Cumi15,BandaAceh,Sumatra,Indonesia eDepartmentofBiologicalSciences,OldDominionUniversity,Norfolk,VA23529,USA
fDepartmentofEcologyandEvolutionaryBiology,UniversityofCaliforniaLosAngeles,LosAngeles,CA90095-7239,USA gMasterprograminEnvironmentalSciences,UdayanaUniversity,JlP.B.Sudirman,Denpasar,Bali,Indonesia
a
r
t
i
c
l
e
i
n
f
o
Articlehistory:
Received9October2014
Receivedinrevisedform4November2014 Accepted9November2014
HandlingEditorProf.GeorgeA.Rose Availableonline11December2014
Keywords:
Shark DNAbarcoding Indonesia
a
b
s
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Sharksareapexpredatorsandkeystonespeciesthathaveaprofoundinfluenceontheecologyand food-webdynamicsofcoralreefsandepipelagicmarineecosystems.However,sharksarebeingheavily overfishedcompromisingthehealthoftheworld’sreefsandpelagicenvironments.AlthoughIndonesia istheworld’slargestandmostdiversecoralreefecosystem,informationontheexploitationofsharks inthisregionisscarce.ResultsofDNAbarcodingofsharkfinrevealedtwoalarmingfindings:(1)a rar-ityofreefsharksthatshoulddominateIndonesia’scoastalecosystems,and(2)afisherythattargets endangeredsharks.Thediversityandnumberofthreatenedspeciesrecoveredinthisstudyhighlights theurgentneedforimprovedregulationandcontrolofIndonesia’ssharkfishery.
©2014ElsevierB.V.Allrightsreserved.
1. Introduction
Asapexpredators,manysharksarekeystonespeciesthathavea significantinfluenceontheecologyandfood-webdynamicsofcoral reefandepipelagicoceanecosystems(Ferrettietal.,2010;Myers etal.,2007).However,sharkpopulationshavedeclinedglobally byupto90%(Myersetal.,2007),largelyasaresultofa multi-billiondollarindustrythatharvestshundredsofmillionsofsharks annually(Chapmanetal.,2013)andlifehistorytraitssuchaslow fecundity,late maturity,and a longgestationperiod that make sharkpopulationsparticularlysensitivetooverfishingandhabitat degradation(Baumetal.,2003).Globalsharkfisheriesarelargely
∗ Correspondingauthorat:TheIndonesianBiodiversityResearchCentre,The AnimalBiomedicalandMolecularBiologyLaboratoryofUdayanaUniversity,Jl Sesetan-Markisa6,Denpasar,Bali80226,Indonesia.Tel.:+623618423061; fax:+62361223791.
E-mailaddress:[email protected](G.N.Mahardika).
drivenbythedemandforsharkfins,akeyingredientintheAsian delicacy,sharkfinsoup.
TheConventiononInternationalTradeinEndangeredSpecies of Wild Fauna and Flora (CITES) currently lists many sharks asAppendixI(speciesthreatenedwithextinction)orAppendix II (species where trade must be regulated to prevent over-utilization).Afurther60sharksandraysarelistedas“vulnerable” or“nearthreatened”(Camhietal.,2009).WhileCITESdesignation shouldpromoteregulationofinternationaltradein shark prod-ucts,theprimarycommodityresultingfromsharkfisheriesarefins. Wholesharksarerarelylandedatcommercialports(Clarkeetal., 2006;Liuetal.,2013)throughoutmuchoftheworld;insteadsharks are“finned”atsea,aprocessbywhichfinsareremovedand bod-iesdiscarded,andthenfinsdriedforsaletowholesalers(Fig.1). Thisprocessiscommonwhethersharksarethetargetedfisheries speciesortheresultofby-catch(Afonsoetal.,2012).Driedfins typ-icallylackkeydiagnosticfeatures,makingidentificationoffinsto species,andthereforeregulationoftradeinfins,extremely chal-lenging.WhileDNAbarcodingbasedona shortfragmentofthe mitochondrialcytochromeoxidaseI(COI)genehasbeenusedto
http://dx.doi.org/10.1016/j.fishres.2014.11.003
Fig.1.Photographsofsharkandshark-finsamplecollection.Sun-driedfins(left)inBali,November1,2011;wholesharkandelasmobranchauctionattheharbourinLombok (right),July12,2012.
Source:IndonesianBiodiversityResearchCentre.
identifyfinstospecies(Holmesetal.,2009;Moftahetal.,2011; Pinhaletal.,2012;Wongetal.,2009),thistechniqueisnotwidely usedtopromoteregulationofsharkfisheries.
Comprisedofmorethan17,000islands,Indonesiaisthelargest geographic areaand heart of the “Coral Triangle”, a six-nation regionofSouthEastAsiathatishometotheworld’smostdiverse seas(Carpenteretal.,2011;DubinskyandStambler,2011;Roberts et al., 2002). Approximately 30% of the world’s shark and ray speciesarepresentinthisregion(LastandStevens,1994)including regionalendemicsuniquetotheCoralTriangleandotherbroadly distributedIndianandPacificOceanspecies(Barnettetal.,2012; Bondetal.,2012;Campanaetal.,2011;Nadonetal.,2012;Oliver etal.,2011).Thehighvalueofsharkfinsonglobalmarketshas sparked rapid growth in shark-fishing in Indonesia focused on supplyingfinstogrowingmarketsinAsia.Comprisedof a mix-tureofcommercialandopportunisticartisanalfisheries,thetotal elasmobranch catch in Indonesia was estimated at more than 110,000 tonnes in 2007 (Camhi et al., 2009), representing the largestrecordedharvestintheworld(Tull,2009).Despitethesize andvalueofIndonesiansharkfisheries,theexpansivenatureof Indonesiacombinedwiththediffusenatureofthesharkfinfishery meansthatbasicfisheriesdataneededforeffectivemanagement andregulationinIndonesia(e.g.speciescomposition,harvest lev-els,etc.)isseverelylacking.
2. Materialsandmethods
Wecollected582sharkfinsfromtraditionalfishmarketsand shark-finexportersacrossIndonesiafrommid-2012tomid-2014, includingAceh,Jakarta,WestJava,CentralJava,EastJava,Bali,West Kalimantan,South Sulawesi,North Sulawesi,Maluku,andWest Papua.Additionalsampleswerecollectedfromsharkfin export warehousesinCilacap(CentralJava)andTanjungLuar(WestNusa Tenggara)(Fig.2).Wesampleda thinsliceof tissuefromdried finsinfishmarkets.Inexportwarehouses,werandomlysampleda minimumoffivecaudalfinsfromboxesoffreshfins.Thetotal num-bersofdriedandfreshfinswere164and418,respectively.Samples werepreservedin96%alcoholforsubsequentDNAanalysis.
Whole DNA was extracted using a simple Chelex protocol (Walshetal.,1991).Afragmentofthemitochondrialcytochrome oxidaseCsubunit-1(COI)wasamplifiedusingAmplyTaqRedTM (AppliedBiosystems)andthestandardfishDNA-barcodingprimers Fish-BCL andFish-BCH(Baldwinetal.,2009).Theamplification parameterswere aninitialdenaturationof94◦C for15min,38
cyclesof94◦Cfor 30s, 50◦C for30s,and 72◦C for45s,witha
finalextensionof72◦Cfor5min.PCRproductswerevisualizedvia
electrophoresisonagarosegelsandethidiumbromidestaining. The COI fragment could be amplified and sequenced from allsamples.Thesequencingwasconducted usingboth forward and reverse directions at the University of California Berkeley SequencingFacility.TheresultwasalignedusingMEGA5(Tamura et al., 2007).We then determined species identity by compar-ing sequences to GenBank and Barcode of Life Data Systems (http://www.boldsystems.org) databases enforcing a sequence homologythresholdof>99%aspreviouslyapplied(Liuetal.,2013).
3. Results
DNAbarcodingofa600–654bpofmitochondrialCOIgene suc-cessfullydeterminedthespeciesidentityof582finscollectedfrom marketsacrosstheIndonesianarchipelagobasedona99%sequence similaritycriterioninGenBankandBarcodeofLifeDataSystems (BOLD)databases.Intotal,analysesdetermined40differentshark species(Table1).Fivespecies(silky,scallopedhammerhead,blue, bigeyethresher,andthreshersharks)representedmorethan50% ofthetotalfinssampled.Silky(19.10%),scallopedhammerhead (10.50%)andbluesharks(8.20%)werethemostcommonspecies recovered,followedbybigeyethresher(7.60%)andthreshersharks (7.20%).Incontrast,29specieswereobservedatlessthan2%ofthe totalsamples,including7speciesthatwererepresentedbyonly oneortwosamples.
Thevastmajorityofthesamples(92%)werelistedas “endan-gered”(1)“vulnerable”(12)or“nearthreatened”(19)whileonly 4specieswerelistedasspeciesofleastconcern.Theremaining 3speciesareclassifiedasdatadeficient.Similarly,83%ofspecies identifiedwerepelagicspeciesofsharkwhileonly17%werereef sharks.
4. Discussion
Fig.2. Samplingsitesofshark-fincollectioninIndonesiaduring2012–2014.ThesiteswereLampulo,BandaAceh(1),Lhokseumawe,BandaAceh(2),Meulaboh,West Aceh(3),Langsa,BandaAceh(4),SimeulueIsland,Aceh(5),MuaraBaru,Jakarta(6),PelabuhanRatu,WestJava(7),PelabuhanPerikananSamudraCilacap,CentralJava(8), PelabuhanPerikananMuncar,EastJava(9),Bali(10),TanjungLuar,Lombok(11),Paotere,Makassar,SouthSulawesi(12),PelabuhanPerikananBitung,NorthSulawesi(13), PasarRemuSorong,WestPapua(14),PasarJimbatanPuriSorong,WestPapua(15),PasarSanggengManokwari,WestPapua(16),PelabuhanSamudraAmbon,Maluku(17), SingkawangWestKalimantan(18).
asspeciesof“leastconcern”.Giventhatsharksarecharacterized bylowfecundity,latematurity,andalonggestationperiod(Baum etal.,2003),thefindingthatnearly93%ofallfinssampledcame fromspecies viewedby IUCN as threatened withextinction or vulnerabletoover-exploitationstronglysuggeststhatIndonesian sharkfisheriesareunsustainable.
Fishing effortfor sharks wasstrong biased with more than 50% of thetotal samplescoming fromfive species: silky, scal-lopedhammerhead,blue,bigeyethresher,and threshersharks. The endangered scalloped hammerhead (CITES Appendix 1) representedmorethan10%ofthetotal finssampled.Most dis-turbing,thishighfrequencyofscallopedhammerheadswasseen acrosssamplinglocations,includingAceh,Java,Lombok,Sulawesi, KalimantanandPapua,indicatingthatfishermanarelikely specif-ically targeting these endangeredsharks acrossthe Indonesian archipelago.Similarly,thevulnerablethresherandbigeyethresher sharkscomprisednearly15%ofthetotalcatch,whilethenearly threatenedsilkyand bluesharksrepresented19.10% and 8.20% respectively.ThehighfrequencyofthesespeciesacrossIndonesia stronglysuggeststhattheyarenottheresultofby-catchor small-scaleartisanalfisheries,butinsteadresultfromlarge-scaletargeted sharkfisheries.
Anotherdisturbingfindingofourstudywasthatthevast major-ity (83%) of the species recovered were pelagic sharks, while commonCarcharhiniformes suchasGalapagos(0.52%),grey reef (01.20%),black-tipreef(3.61%),andwhite-tipreefshark(0.86%) thattypicallydominatecoralreefecosystemswereextremelyrare aswerecommonreefOrectolobiformes,suchastawnynurse(1.37%) andbrown-bandedbamboo(0.86%)sharks.Onpristinecoralreefs, reefsharksmake upa nearly63% oftotal fishbiomass(Sandin etal.,2008).BecausethegreatestfishingpressureinIndonesian watersisinshallowcoastalareaswherereefsharkstypicallythrive, thealarminglylownumberofreefsharksrecoveredinour sam-plingstronglyindicatesthatreef-sharkpopulationsinIndonesia havecollapsed,mostlikeduetooverfishing(AllenandErdmann, 2012)ashappenedintheGreatBarrierReef(Robbinsetal.,2006),
and/orreefdegradation(Burkeetal.,2011).Lowincidenceofreef sharksisconsistentwiththerarityofsharksightingsduringscuba activitiesacrossmostofIndonesia,withtheexceptionofregions ofEasternIndonesiasuchasRajaAmpat(M.Erdmann,pers. com-mun.).Indeedresultsshowthat18reefsharkfinswereidentified fromsamplesinWesternIndonesiaand19inJava,whereas32and 36wereidentifiedfromEasternIndonesiaandCentralIndonesia. Eventhemostcommonreefsharkinoursampling,theblacktip, wasnotobservedin75%ofsamplinglocationsand59%of black-tipfinscamefromonelocalityinPapua.Thesedatasuggestthat manyreefsharksmaybeecologicallyextinctinpartsofIndonesian waters.
While sampling revealedthat a diversity of sharks entering the Indonesian shark fin trade, three species represented new records for Indonesia, including the western spotted gummy, galapagos, andwhitecreek sharks.It is notclearwhetherthese sharkswerecaughtwhilemigratingthroughIndonesianwatersor whetherthereareresidentpopulations.Iftheformeristrue,fishing pressureswithinIndonesianwaterscouldhaveanegativeimpact onresidentpopulationsoutsideIndonesia.Ifthelatteristrue,the rarityofthesespeciesinoursamplemayindicatethattheir popu-lationsareheavilydepressed,requiringspecialconservationstatus withinIndonesia.
Table1
Distribution,catchfrequency,IUCN/CITESstatusofvarioussharkspeciesharvested indifferentgeographicalareasinIndonesia.
No Species Total Frequency IUCNstatus
1 Carcharhinus falciformis
111 19.07% Nearthreatened
Silkyshark
2 Sphyrnalewini 61 10.48% Nearthreatened
Scalloped hammerhead
3 Prionaceglauca 48 8.25% Endangered
Blueshark 4 Alopias
superciliosus
44 7.56% Vulnerable
Threshershark
5 Alopiaspelagicus 42 7.22% Vulnerable
Bigeyethresher shark
6 Carcharhinussorrah 39 6.70% Nearthreatened Spottailshark
7 Carcharhinus limbatus
21 3.61% Nearthreatened
Blacktipshark
8 Isurusoxyrinchus 21 3.61% Vulnerable
Shortfinmako 9 Rhizoprionodon
acutus
18 3.09% Leastconcern
White-eyedshark
10 Squalushemipinnis 17 2.92% Nearthreatened
Indonesian shortsnoutspurdog
11 Galeocerdocuvier 12 2.06% Nearthreatened
Tigershark
12 Isuruspaucus 11 1.89% Vulnerable
Longfinmako 13 Carcharhinus
longimanus
10 1.72% Vulnerable
Whitetipoceanic shark
14 Centrophorus niaukang
10 1.72% Nearthreatened
Taiwangulper shark 15 Carcharhinus
melanopterus
9 1.55 Nearthreatened
Blacktipreefshark
16 Carcharhinussealei 9 1.55% Nearthreatened
Blackspotshark 17 Carcharhinus
brevipinna
9 1.55% Nearthreatened
Spinnershark 18 Hemipristis
elongata
8 1.37% Leastconcern
Snaggletoothshark
19 Nebriusferrugineus 8 1.37% Vulnerable
Tawnynurseshark 20 Carcharhinus
amblyrhynchos
7 1.20% Nearthreatened
Greyreefshark
21 Hemitriakisfalcata 7 1.20% Leastconcern
Sicklefinhound shark 22 Mustelus
lenticulatus
7 1.20% Leastconcern
Spotted smoothhound 23 Hemigaleus
microstoma
6 1.03% Vulnerable
Sicklefinweasel shark
24 Loxodon macrorhinus
6 1.03% Leastconcern
Jordan’sblue dogshark
25 Sphyrnazygaena 6 1.03% Vulnerable
Smooth hammerhead
Table1(Continued)
No Species Total Frequency IUCNstatus
26 Chiloscyllium punctatum
5 0.86% Nearthreatened
Brownbanded bambooshark
27 Triaenodonobesus 5 0.86% Nearthreatened
Whitetipreefshark 28 Hemitriakis
indroyonoi
4 0.69% Datadeficient
Indonesian houndshark 29 Carcharhinus
albimarginatus
4 0.69% Nearthreatened
Silvertipshark 30 Carcharhinus
galapagensis
3 0.52% Vulnerable
Galapagosshark 31 Carcharhinus
plumbeus
3 0.52% Vulnerable
Sandbarshark
32 Squalusmontalbani 2 0.34% Vulnerable
Philippines spurdog
33 Squatinalegnota 2 0.34% Datadeficient
Indonesian angleshark
34 Carcharhinusleucas 1 0.17% Nearthreatened
Bullshark 35 Carcharhinus
amboinensis
1 0.17% Datadeficient
Pigeyeshark 36 Carcharhinus
coatesi
1 0.17% Datadeficient
Whitecreekshark
37 Heptranchiasperlo 1 0.17% Nearthreatened
Sharpnose sevengillshark 38 Pseudocarcharias
kamoharai
1 0.17% Nearthreatened
Crocodileshark 39 Atelomycterus
marmoratus
1 0.17% Nearthreatened
Coralcatshark 40 Carcharhinus
obscurus
1 0.17% Vulnerable
Duskyshark
Indonesia’smarineecosystemsareanextremelyvaluable nat-uralresource that contributes significantlytoits GDPand food needsofitspeople(Barberetal.,2014).Becauseoftheimportance of sharks in maintaininghealthy marine ecosystems,achieving thebiodiversitypreservationandfoodsecuritygoalsoftheCoral Triangle Initiative (www.coraltriangleinitiative.org)will require enforcementofexisting fisheriesregulationsand expandingthe management of shark fisheries to protect ecologically impor-tant, but highly threatened shark species. Recently, the West Papua Province enacted regulations prohibiting the capture of sharks,raysandcertainotherfishspeciesinRajaAmpatwaters (www.rajaampatkab.go.id/index.php).This initiative serves as a modelthat couldbeadoptedandenforced byotherdistrictsin Indonesia to prevent a further decline in Indonesia’s vulnera-ble sharkpopulation,furtherjeopardizingitsalreadyimperilled marineecosystems(Burkeetal.,2011).
5. Conclusion
Acknowledgements
This study was funded by the Partnerships for Enhanced EngagementinResearch(PEER)ScienceProgramme (AID-OAA-A-11-00012)funded bytheUnitedStates AgencyforInternational Development(USAID)andtheNationalScienceFoundation(NSF) inpartnershipwithNSFPIREProgramme(OISE-0730256). Facil-itiesandtrainingforthisstudywereprovidedbyUCLAandthe SmithsonianInstitution under USAID (grant number 497-A-00-10-00008-00). We thank B. Subhan,A.A. Wibowo, I.A.Putra,S. Bahri,Rahmad, N.Akbar,P. Akna,WWF Indonesia,D.Suprapti, Agri,Masriana,ReefCheckIndonesia,P.Borsa,N.Putra,A. Yusma-linda,Ambariyanto,S.Indriawan,A.A.Tarekat,Stevanus,A.Arimbi, C.A.K.Hardani,Ma’rufah,A.Kusumafortheirassistancewith sam-pleand/ordatacollection.
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