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Mammal records of two visits to Pulau Bintan, Riau Archipelago, Indonesia in 2018

Authors:
  • WWF-Hong Kong

Abstract and Figures

Report of mammal species recorded on Bintan Island, Riau Archipelago, Indonesia during two visits in 2018
Figure 2. Identity of subjects and descriptions of records: 1) Common Treeshrew, Tupaia glis (Mammalia: Scandentia: Tupaiidae), Seen daily in forest interior and the resort grounds in September (Fig. 3). Individuals were seen, always on the ground, throughout daylight hours including one raiding a rubbish bin at noon. 2) Long-tailed Macaque, Macaca fascicularis (Mammalia: Primates: Cercopithecidae), Common, observed daily in both forest interior, golf courses and resort grounds, with troops of up to 30 individuals seen on both trips (Fig. 4). 3) Silvery Lutung (Silvered Leaf Monkey), Trachypithecus cristatus (Mammalia: Primates: Cercopithecidae), Seen daily on both trips, active at dawn and dusk in patches of mature inland as well as coastal forests (Fig. 5). The biggest troop consisted of 8 individuals with juveniles and infants, and a troop was seen feeding on the cauliflorous fruits of a fig tree (Ficus sp.). It is listed as Near Threatened in the IUCN Red List. 4) Plantain Squirrel, Callosciurus notatus (Mammalia: Rodentia: Sciuridae), Seen daily on both trips, most visible in resort grounds and golf courses, where some individuals are habituated (Fig. 6). 5) Small-toothed Palm Civet, Arctogalidia trivirgata (Mammalia: Carnivora: Viverridae), One adult observed on 28 July at 21:30 hrs, resting ca. 10 metres from the ground in a tall tree in a patch of tall dipterocarp forest with disturbed undergrowth (Fig. 7). When revisited an hour later it was active in nearby tall trees, then it moved out of sight.
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21
SEAVR2018:021025
ISSN:24248525
Dateofpublication:26January2019
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MammalrecordsoftwovisitstoPulauBintan,RiauArchipelago,
Indonesiain2018
BoscoP.L.CHAN&VickyW.K.Chan
boscokf@kfbg.org(BPLChan),button153@gmail.com(VWKChan)
Observers:BoscoP.L.Chan,VickyW.K.Chan.
Photographsby:BoscoP.L.Chan.
Subjectsidentifiedby:BoscoP.L.Chan,EricJ.Sargis(Tupaiaglis).
Location:PulauBintan,RiauArchipelago,Indonesia.
Elevation:Sealeveltoca.50metres
Habitat:Smallpatchesofoldgrowthdipterocarpforest(Fig.1),secondaryforestofvarioussuccessionalstages
(Fig.2),golfcourses,resortgroundsanddisturbedgrasslandshrublandmosaic.Theprofusionofpalms(Family
Arecaceae)andpandans(FamilyPandanaceae)areprominentfeaturesinthenaturalforestoftheisland.
Datesandtimes:2529July2018,1417September2018,dayandnight.
Figure1. Figure 2.
Identityofsubjectsanddescriptionsofrecords:
1) CommonTreeshrew,Tupaiaglis(Mammalia:Scandentia:Tupaiidae),
SeendailyinforestinteriorandtheresortgroundsinSeptember(Fig.3).Individualswereseen,alwaysonthe
ground,throughoutdaylighthoursincludingoneraidingarubbishbinatnoon.
2) LongtailedMacaque,Macacafascicularis(Mammalia:Primates:Cercopithecidae),
Common,observeddailyinbothforestinterior,golfcoursesandresortgrounds,withtroopsofupto30
individualsseenonbothtrips(Fig.4).
3) SilveryLutung(SilveredLeafMonkey),Trachypithecuscristatus(Mammalia:Primates:Cercopithecidae),
Seendailyonbothtrips,activeatdawnandduskinpatchesofmatureinlandaswellascoastalforests
(Fig.5).Thebiggesttroopconsistedof8individualswithjuvenilesandinfants,andatroopwasseenfeeding
onthecauliflorousfruitsofafigtree(Ficussp.).ItislistedasNearThreatenedintheIUCNRedList.
4) PlantainSquirrel,Callosciurusnotatus(Mammalia:Rodentia:Sciuridae),
Seendailyonbothtrips,mostvisibleinresortgroundsandgolfcourses,wheresomeindividualsare
habituated(Fig.6).
5) SmalltoothedPalmCivet,Arctogalidiatrivirgata(Mammalia:Carnivora:Viverridae),
Oneadultobservedon28Julyat21:30hrs,restingca.10metresfromthegroundinatalltreeinapatchof
talldipterocarpforestwithdisturbedundergrowth(Fig.7).Whenrevisitedanhourlateritwasactivein
nearbytalltrees,thenitmovedoutofsight.
22
6) Sambar,Rusaunicolor(Mammalia:Artiodactyla:Cervidae),
Threemales,witheithervelvetedorhardenedantlers,wereseeninRiaBintanGolfClub(Fig.8).Sambaris
notconsideredtobepartofnativeBintanfauna(Dammerman,1926,Meijaardetal,2007).Aninterviewwith
themanagementrevealedthatsomedeerwereimportedfromKalimantanbythenowclosedLagoiZoo.One
maleand3femalesweregiventothegolfclubaroundtheyear2013,whichbredincaptivityandwerelater
released.Abreedinggroupof1720deerarecurrentlyroamingfreelyinthevicinityofthegolfcourseand
surroundingforest,andcomeouttograzeonthefairways.TheBorneansubspeciesRu.brookeiisendemicto
Borneo.SambarislistedasVulnerableintheIUCNRedList.
7) EurasianWildPigorBeardedPig,Sussp.(Mammalia:Artiodactyla:Suidae),
BoththeBeardedPig(Susbarbatus)andtheEurasianWildPig(S.scrofa)havebeenreportedfromBintan
Island(Dammerman,1926;websiteofIUCNSSCWildPig,Peccary&HippoSpecialistGroups).Photographs
takenbyhandphoneswereshowntotheauthorsbytwoseparatelocalinhabitants,butthephotoqualities
precludeddefinitivespecieslevelidentification.Sadly,onesetofphotosdepictedapighuntingeventoutside
theBintanResortsarea.Theothersetofphotosshowedafamilygroupofpigsindaylightcrossingapaved
roadnearRiaBintanGolfClub.Diggingsbypigswereobservedbytheauthorsinforestinteriornearby,and
golfcourseworkersalsoreportedbabihutan(“forestpig”inBahasaIndonesia)arecommon,whichcouldbe
eitherspecies.
Remarks:TheauthorspaidtwovisitstothenortherncoastofPulau(=Island)Bintan,intheRiauArchipelago,
Indonesia,whichliessome40kmsouthofSingapore.Thenorthernpartoftheislandhasbeendevelopedfor
internationaltourismwithresortsandassociatedfacilitiesofdifferentscales,andisknowncollectivelyasthe
“BintanResorts”.Despitethedevelopment,thelandscapeofBintanResortsispredominatelycoveredin
secondary(includingpeatswamp)forestsofvarioussuccessionalstages,withsmallpatchesofoldgrowth
dipterocarpandoriginalpeatswampforests.
WithregardstotheCommonTreeshrew,thesubspeciesT.g.castaneaisendemictoBintanIslandwithadistinct
pelage(theexampleinFigure3hasamarkedlyreddishtail).Sargisetal.(2017)considertheBintansubspecies,
togetherwiththepopulationfromnearbyMapurIsland,tobeuniqueamongstcommontreeshrews,and“…have
aclearlydistinctivepelagethatsuggestsaffinitywithaspeciesotherthanT.glisi.e.itcouldpotentiallybea
separatespecies,orrelatedtotheRuddyTreeshrewT.splendidulaspeciescomplex.
Figure3.CommonTreeshrew,Tupaiag
l
is
23

Figure4.LongtailedMacaque,Macacafascicularis
Figure5.SilveryLutung,Trachypithecuscristatus
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Figure6.PlantainSquirrel,Callosciurusnotatus
Figure7.SmalltoothedPalmCivet,Arctogalidiatrivirgata
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Figure8.Sambar,Rusaunicolor
Allimages©BoscoP.L.Chan
Regardingtheidentityof“forestpigs”onPulauBintan,theBeardedPigsubspeciesS.b.barbatuswaspreviously
recordedontheislandbutwasreportedlyextirpated;thisspeciesisinrapiddeclinegloballyandislistedas
VulnerableintheIUCNRedList(Luskinetal.,2017).TheEurasianWildPighasbeenreportedasfairlycommon
throughoutnorthernBintan(Subaraj,1994).Fieldidentificationofthesetwospeciescanbechallengingand,in
viewoftheabsenceofrecentbiodiversitysurveysforBintanIslandandtheresilienceofpigspeciestosurviveon
fragmentedanddegradedforest,bothspeciescouldstillbepresent.Itwouldbeinterestingtoconductsurveysto
clarifytheidentification,distributionandstatusofwildpigsonBintan.
References:
Dammerman,K.W.(1926).ThefaunaofDurianandtheRhioLinggaArchipelago.Treubia8:281326.
IUCNSSCWildPig,Peccary&HippoSpecialistGroups.(undated).EurasianWildPig(Susscrofa)
https://sites.google.com/site/wildpigspecialistgroup/home/Susscrofa
Luskin,M.,Ke,A.,Meijaard,E.,Gumal,M.&Kawanishi,K.2017.Susbarbatus(errataversionpublishedin2018).
TheIUCNRedListofThreatenedSpecies2017:e.T41772A123793370.http://dx.doi.org/10.2305/IUCN.UK.2017
3.RLTS.T41772A44141317.en.Accessedon22December2018
Meijaard,E.,Sheil,D.,Nasi,R.,Augeri,D.,Rosenbaum,B.,Iskandar,D.,Setyawati,T.,Lammertink,M.,Rachmatika,
I.,Wong,A.,Soehartono,T.,Stanley,S.andO’Brien,T.(2007)Lifeafterlogging:Reconcilingwildlifeconservation
andproductionforestryinIndonesianBorneo(revisededition).Bogor,Indonesia:CIFOR
Sargis,E.J.,Woodman,N.,Morningstar,N.C.,Bell,T.N.andOlson,L.E.2017.Skeletalvariationandtaxonomic
boundariesamongmainlandandislandpopulationsofthecommontreeshrew(Mammalia:Scandentia:Tupaiidae).
BiologicalJournaloftheLinneanSociety120(2):286312.
Subaraj,R.1994.RecordsfromnorthernPulauBintan,RiauIslands,Indonesia.Pangolin:abulletinonSingapore
vertebrates.VertebrateStudyGroup(NatureSocietySingapore)7:1617.
ResearchGate has not been able to resolve any citations for this publication.
Technical Report
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Cycloderma aubryi inhabits a large range with little to moderate habitat degradation, but is exploited throughout its range for local consumption; this exploitation level is intensive enough to have led to documented declines at least locally, and possibly across much of its range. With an estimated generation time of 20 years, past declines and anticipated continuing or intensifying exploitation likely exceed a 30% overall range-wide decline of the species, thus qualifying the species as Vulnerable A2bd + 4bd. Cycloderma aubryi was last assessed as Least Concern in 1996, and was therefore not included on the Red List at that time. Citation: Chirio, L., Diagne, T. & Pauwels, O.S.G. 2017. Cycloderma aubryi . The IUCN Red List of Threatened Species 2017: e.T163448A1009393. https://dx.doi.org/10.2305/IUCN.UK.2017-3.RLTS.T163448A1009393.en.
Article
Full-text available
Treeshrews (order Scandentia) include 23 currently recognized species of small-bodied mammals from South and Southeast Asia. The taxonomy of the common treeshrew, Tupaia glis, which inhabits the Malay Peninsula south of the Isthmus of Kra, as well as a variety of offshore islands, has an extremely complicated history resulting from its wide distribution and subtly variable pelage. In our ongoing investigation of species boundaries in Tupaia, we compared island and mainland populations of T. glis using multivariate analyses. Specifically, we compared the skull and hand morphology of 13 island populations, most of which have been recognized as separate species or subspecies, to that of the mainland population. Island populations generally average smaller body size than those on the mainland, but none of the island populations are sufficiently distinct from the mainland population to warrant species recognition. This has important conservation implications for this widespread and morphologically variable species. It also highlights the potential role that ecogeographic explanations can play in understanding intraspecific variation, a role that should be considered in taxonomic studies and investigated further in T. glis and other treeshrews.
Book
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Deforestation, forest degradation and hunting are having an increasing impact on wildlife in Borneo and many species are threatened. The Indonesian government has pledged to do its best to control these problems, a pledge that has been formalized in a range of laws and international agreements. But despite the need for immediate and defi nitive actions, achieving conservation goals remains fraught with challenges. Part of the problem is that conservation interest has focused on protected and unlogged forest, but we need to recognise that logged forest is a vital component of any comprehensive approach to landscape-scale conservation. Our review focuses on the ecological and life history aspects of Bornean vertebrates and how these relate to forest management, with a specifi c emphasis on lowland and hill dipterocarp forest. But ecological studies seldom lead to improved forest management practices. Our review provides three responses to this: 1. Recommendations in the research literature are compiled and translated into management implications. These can be presented to those who need to know about them. 2. Knowing that a species declines with forestry interventions is seldom enough to clarify how forestry practices might be adapted (short of a ban) in order to mitigate the negative impacts. We set out to link species sensitivity with ecological and life history correlates to develop a better understanding of why a given taxon is vulnerable, allowing a more species-specifi c approach to the protection of habitat characteristics and components. 3. Research needs to answer management relevant questions. We identify priority topics for research. Our primary intention is thus to identify and clarify what makes fauna vulnerable to various kinds of forestry-related interventions. Based on these results, insights and related hypotheses, we compile and develop recommendations for improved management practices and identify priorities for future research. We are pragmatic we acknowledge the critical role of the socio-political context for implementing our proposals. Yet, while various key issues are raised, the pace of change in Indonesia is currently so rapid and the issues so complex that our discussion of this context cannot resolve all the current and future opportunities. We focus, therefore, on technical ecological information, the validity of which is independent of volatile local politics. We found a considerable body of ecological information relevant to the management of tropical forests and their wildlife. Improving current management practices requires collaborations between ecologists and forest managers to develop pragmatic guidance for improved practices. The present review and synthesis is one component in achieving this collaboration, focusing upon the fauna of the Malinau area in East Kalimantan (Indonesia). In Part I of this book we summarize knowledge concerning various forest interventions and how they affect selected wildlife species. We identify a range of effects caused by timber harvesting, and note the associated infl uences of hunting and forest fragmentation. Additional problems are caused by exotic species, law enforcement, fi res and a range of other factors. Yet despite decades of wildlife research on Borneo there is little information on the magnitude and mechanisms of threats to wildlife. Most studies considered in this book report on autecological studies of various species, but do not analyse species characteristics in relation to different threat levels. Still, we are able to draw various conclusions about the effects of timber harvesting and associated factors on wildlife, and provide general management recommendations. Selective logging has fewer direct negative consequences for many vertebrate species than is sometimes assumed. It certainly affects certain groups of species, like terrestrial, insectivorous birds and mammals, which suffer from the reduced ground cover. This may primarily be caused by the slashing of ground cover and lianas, which is currently required by law. Some species, though, such as deer and banteng, appear well adapted to, and can increase in, the more open habitats that follow logging. Timber harvesting generally brings a number of associated problems in addition to the direct disturbance of forest habitat. Two important aspects, from a wildlife conservation perspective, are increased hunting and forest fragmentation. Hunting can pose a considerable threat to some forest fauna and this threat often increases with forestry roads, increased access to forests and the provisioning needs of camps. Improved hunting technologies and increasing availability of guns add to the pressure. Roads, skid trails and degraded areas fragment forest habitats. Small isolated populations, such as those created by fragmented or heavily harvested landscapes, are at much greater risk of various deleterious effects that can ultimately lead to local extinction. Some species have minimum fragment size requirements for population persistence. Recent research has highlighted the importance of maintaining ‘forest-like’ habitats, or a network of ‘forest stepping-stone’ habitats in the intervening landscape. The effects seem likely to be worst in forests with excessive road density, wide clearings, and many large deforested openings. Forest edges can generate signifi cant effects on individual, population, and community dynamics in remaining forest areas. Several studies report that the effects of logging can extend considerable distances into surrounding undisturbed forests.
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