DOCSLIB.ORG

Hemigalus Derbyanus, Banded Civet

Total Page：16

File Type：pdf, Size：1020Kb

Download full-text PDF Read full-text
Hemigalus Derbyanus, Banded Civet The IUCN Red List of Threatened Species™ ISSN 2307-8235 (online) IUCN 2008: T41689A45216918 Hemigalus derbyanus, Banded Civet Assessment by: Ross, J. et al. View on www.iucnredlist.org Short citation: Ross, J. et al. 2015. Hemigalus derbyanus. The IUCN Red List of Threatened Species 2015: e.T41689A45216918. http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T41689A45216918.en [see full citation at end] Copyright: © 2015 International Union for Conservation of Nature and Natural Resources Reproduction of this publication for educational or other non-commercial purposes is authorized without prior written permission from the copyright holder provided the source is fully acknowledged. Reproduction of this publication for resale, reposting or other commercial purposes is prohibited without prior written permission from the copyright holder. For further details see Terms of Use. The IUCN Red List of Threatened Species™ is produced and managed by the IUCN Global Species Programme, the IUCN Species Survival Commission (SSC) and The IUCN Red List Partnership. The IUCN Red List Partners are: BirdLife International; Botanic Gardens Conservation International; Conservation International; Microsoft; NatureServe; Royal Botanic Gardens, Kew; Sapienza University of Rome; Texas A&M University; Wildscreen; and Zoological Society of London. If you see any errors or have any questions or suggestions on what is shown in this document, please provide us with feedback so that we can correct or extend the information provided. THE IUCN RED LIST OF THREATENED SPECIES™ Taxonomy Kingdom Phylum Class Order Family Animalia Chordata Mammalia Carnivora Viverridae Taxon Name: Hemigalus derbyanus (Gray, 1837) Common Name(s): • English: Banded Civet, Banded Palm Civet Taxonomic Notes: The taxonomy of Banded Civet has not been recently reviewed. Two proposed subspecies in particular have small ranges on the Mentawai islands, and might have conservation needs; of these H. d. minor has been generally acknowledged as valid, but H. d. sipora was combined with H. d. derbyanus from Sumatra by Pocock (1933); the validity of uniting these subspecies is unclear (Schreiber et al. 1989). Assessment Information Red List Category & Criteria: Near Threatened ver 3.1 Year Published: 2015 Date Assessed: March 3, 2015 Justification: Banded Civet has a large geographic range that includes Borneo, Sumatra (including the Mentawai Islands), Peninsular Malaysia, Peninsular Thailand and Peninsular Myanmar. Across its distribution it occurs over a wide elevation range. Camera-trap surveys, particularly in Malaysian Borneo and Sumatra, have recorded Banded Civet frequently relative to other carnivores. They indicate that it is forest dependent, but can tolerate some habitat disturbance, although there is no evidence that it can survive in agricultural plantations. Continuing loss of natural forest throughout its range makes it reasonable to assume that its population is in decline. The decline rate, driven by loss of habitat compounded by hunting, is difficult to assess and possibly varies much within its range, but it is unlikely that overall it is exceeding 30% (the threshold for Vulnerable) over three generations (taken as 15 years; Pacifici et al. 2013). It is assumed to be more likely to be around 25%, thereby qualifying the species for Near Threatened (nearly meets criteria A2, A3 and A4). Previously Published Red List Assessments 2008 – Vulnerable (VU) – http://dx.doi.org/10.2305/IUCN.UK.2008.RLTS.T41689A10515759.en 1996 – Lower Risk/least concern (LR/lc) Geographic Range Range Description: Banded Civet occurs in the Sundaic subregion: in Peninsular Myanmar (Pocock 1939), Peninsular © The IUCN Red List of Threatened Species: Hemigalus derbyanus – published in 2015. 1 http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T41689A45216918.en Thailand (Kitamura et al. 2010, Chutipong et al. 2014), Malaysia (Peninsular: e.g., Kawanishi and Sunquist 2004, Hedges et al. 2013; Malaysian Borneo: e.g., Mathai et al. 2010, Matsubayashi et al. 2011), Indonesia (Mentawai Islands [Sipora Island, South Pagai Island], Kalimantan, Sumatra; e.g., Schreiber et al. 1989, Holden 2006, Samejima and Semiadi 2012) and Brunei (Bennett 2014). The northernmost Thai record is from 12°53′N (Chutipong et al. 2014) and the northernmost in Myanamr is from 10°09′N (Than Zaw et al. 2008). Several sources list Banded Civet for Vietnam, but no credible evidence of wild occurrence has been traced and it is unlikely to occur there naturally. There are no recent records in Myanmar (Than Zaw et al. 2008). It has been camera-trapped at several locations in peninsular Thailand (Chutipong et al. 2014) and Malaysia (Hedges et al. 2013, S. Mohamad pers. comm. 2014). On Borneo, it is one of the most frequently detected small carnivores in most spot- lighting and camera trap surveys in Sabah, where it has been recorded across the state (Payne et al. 1998, Brodie and Giordano 2011, Ross et al. in prep. a). It is also one of the more frequently detected species in Sarawak (e.g. Mathai 2010). In Kalimantan it has not been recorded in the peat-swamp forests of Sabangau National Park (Cheyne et al. 2010), but it has been detected in peat swamp forest in Berbak National Park, Sumatra (ZSL Indonesia programme pers. comm. 2014). In Sumatra, Holden (2006) detected the species infrequently in lowland primary forest in Kerinci Seblat National Park; however in Bukit Barisan Selatan National Park it is found commonly at higher elevations (McCarthy and Fuller 2014, H. Wibisono pers. comm. 2014). It has been found from sea-level up to 1,660 m a.s.l. (WWF-Malaysia pers. comm. 2014). Country Occurrence: Native: Brunei Darussalam; Indonesia (Kalimantan, Sumatera); Malaysia (Peninsular Malaysia, Sabah, Sarawak); Myanmar; Thailand © The IUCN Red List of Threatened Species: Hemigalus derbyanus – published in 2015. 2 http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T41689A45216918.en Distribution Map © The IUCN Red List of Threatened Species: Hemigalus derbyanus – published in 2015. 3 http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T41689A45216918.en Population Holden (2006) speculated that Banded Civet might typically be rare where it is found. However, Payne et al. (1998) stated that it was the second-most commonly recorded civet in the forests of Sabah and more recent surveys suggest that it is still relatively common in many areas across the state (Ross et al. in prep. a). All evidence suggests that it is forest dependent and so the population is likely to be in decline. Although it has been detected in logged forest (Ross et al. in prep. a) it is likely to occur at lower densities in these areas (Brodie et al. 2014a,b). Current Population Trend: Decreasing Habitat and Ecology (see Appendix for additional information) Banded Civet has been found at elevations up to 1,660 m (WWF-Malaysia pers. comm. 2014). Most records traced by Jennings et al. (2013) were from below 900 m, although this could simply reflect low survey effort at higher elevations within most of its range. Where effort has been made in high- elevation areas it has been found to occur commonly well over 900 m. For example, in Crocker Range National Park, Sabah, Malaysia, it was detected at 75% of camera-trap stations and was the second- most frequently recorded civet; camera-traps in this survey were set between 383 and 1,452 m a.s.l. with 66% of them above 900 m a.s.l. (A.J. Hearn, J. Ross and D.W. Macdonald pers. comm. 2015). At high elevations in the Kelabit Highlands, Sarawak and the Ulu Baram, Sarawak, Banded Civet was the most frequently recorded civet; at high elevations in the Ulu Padas, Sabah, it was the most frequently recorded carnivore (J. Brodie et al. pers. comm. 2014). Banded Civet has been recorded in primary forest (e.g., Wells et al. 2005, Chutipong et al. 2014), logged forest (e.g., Brodie and Giordano 2011, Wilting et al. 2010, Mathai et al. 2010, Hedges et al. 2013) and infrequently from oil palm plantations (A.J. Hearn and J. Ross pers. comm. 2014; Yue et al. in prep.) and acacia plantation landscapes (Belden et al. 2007), but abundance is likely to be lower in modified habitat (Brodie et al. 2014a,b). In Sabah it was shown that its proportion of area occupied was greatly affected by the past logging histories and the species was distributed much more widely and was recorded more often in less disturbed, well managed forest reserves than in forests where conventional logging had caused greater disturbance (Sollmann et al. in prep). It is nocturnal (Lekagul and McNeely 1977, Ross et al. in prep. b). Davis (1962) found in Borneo that over 90% of its diet was insects, and no analysed stomach contents contained fruit or leaves. Systems: Terrestrial Use and Trade Banded Civet is taken as part of general mammal hunting for food across its range. There is no evidence of specific targeting by hunters. Threats (see Appendix for additional information) Habitat loss and degradation have been assumed to be major threats to Banded Civet (Schreiber et al. 1989). Reduction in primary forest has proceeded very fast throughout the lowland Sundaic region in the last 20 years, particularly at lower elevations (e.g. Holmes 2000, BirdLife International 2001, Jepson et al. 2001, McMorrow and Talip 2001, Lambert and Collar 2002, Kinnaird et al. 2003, Curran et al. 2004, © The IUCN Red List of Threatened Species: Hemigalus derbyanus – published in 2015. 4 http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T41689A45216918.en Fuller 2004, Eames et al. 2005, Stibig et al. 2014). This will have caused population declines. Local occurrence of Banded Civet in Borneo is lower in logged areas than in unlogged areas (Brodie et al. 2014a,b). The Mentawai populations are impacted by economic development as human settlements expand into civet habitat, which also may result in conflicts since this species will prey on domestic livestock such as chickens (Schreiber et al.
Load more

Recommended publications
  • Controlled Animals
    Environment and Sustainable Resource Development Fish and Wildlife Policy Division Controlled Animals Wildlife Regulation, Schedule 5, Part 1-4: Controlled Animals Subject to the Wildlife Act, a person must not be in possession of a wildlife or controlled animal unless authorized by a permit to do so, the animal was lawfully acquired, was lawfully exported from a jurisdiction outside of Alberta and was lawfully imported into Alberta. NOTES: 1 Animals listed in this Schedule, as a general rule, are described in the left hand column by reference to common or descriptive names and in the right hand column by reference to scientific names. But, in the event of any conflict as to the kind of animals that are listed, a scientific name in the right hand column prevails over the corresponding common or descriptive name in the left hand column. 2 Also included in this Schedule is any animal that is the hybrid offspring resulting from the crossing, whether before or after the commencement of this Schedule, of 2 animals at least one of which is or was an animal of a kind that is a controlled animal by virtue of this Schedule. 3 This Schedule excludes all wildlife animals, and therefore if a wildlife animal would, but for this Note, be included in this Schedule, it is hereby excluded from being a controlled animal. Part 1 Mammals (Class Mammalia) 1. AMERICAN OPOSSUMS (Family Didelphidae) Virginia Opossum Didelphis virginiana 2. SHREWS (Family Soricidae) Long-tailed Shrews Genus Sorex Arboreal Brown-toothed Shrew Episoriculus macrurus North American Least Shrew Cryptotis parva Old World Water Shrews Genus Neomys Ussuri White-toothed Shrew Crocidura lasiura Greater White-toothed Shrew Crocidura russula Siberian Shrew Crocidura sibirica Piebald Shrew Diplomesodon pulchellum 3.
    [Show full text]
  • Borneo, Malaysia) 2019 October 7Th-31St Lennart Verheuvel
    Tripreport Sabah (Borneo, Malaysia) 2019 October 7th-31st Lennart Verheuvel www.shutterednature.com Sabah October 7th till October 31st. This was the second part of the trip I had planned to do after my studies were finished. Initially the plan was to go to Borneo for three months, I actually have asked for advice on the forum of Mammalwatching.com for that. Later I decided to change my mind and go for South-America, even later I decided to go for a combo: first three months South-America and then three weeks in Borneo. The road to Borneo was a long and bumpy one and I also ran into some difficulties during the trip, but in the end it was all worth it. The funny thing was that literally a week before my plane left, I still wasn’t sure if I could go, so looking back I’m really glad it all worked out. I travelled by myself but I did the first thirteen days of the trip together with Duncan McNiven and Debbie Pain from England and later we did our first five nights in Deramakot with Stuart Chapman and Nick Cox. It was nice searching for mammals (and birds) with these guys and it was really cool that the four of use managed to see Clouded Leopard together on one of the last nights of Stuart and Nick. I did fly on Tawau, which is not the nearest airport if you want to go to Danum but that was because I was first supposed to go with someone else, who backed out last minute and it was too expensive to change the destination.
    [Show full text]
  • A Note on Coat Colour Variation in Common Palm Civet Paradoxurus Hermaphroditus
    Coat colour variation in Common Palm Civet SHORT COMMUNICATION A note on coat colour variation in Common Palm Civet Paradoxurus hermaphroditus H. CHUNEKAR1*, A. PARDESHI2, C. GULAWANI3 & R. SHINDE4 1. 11+12, Sangeeta society, Vanaz corner, Kothrud, Pune-411038, Maharashtra, India. Abstract. 2. 557, Ghorpade Peth, Shrinivas Apts., Pune 411042, Maharashtra, India. We report coat colour variations in Common Palm Civet Paradoxurus hermaphroditus based on the 3. 1081, Sadashiv Peth, Omkar Apts., observations from Karnataka and Maharashtra states, India. In both cases, individuals resemble each Pune 411030, Maharashtra, India. other in terms of brownish patch on the back, lack of black pigmentation on the leg extremities and 4. New Mhada colony, 409 Sadarbazar, approximately half of the tail length with white coat colour unlike typical Common Palm Civet. Satara L-2/A/58 Pin. 415001 उदमा車जरातील (Paradoxurus hermaphroditus ) वेगळ्या र車गस्व셂पाची न 車द Correspondence: सारा車श H. Chunekar [email protected] भारतातील महाराष्ट्र आणि क셍ााटक येथू셍 셍 ोंदवलेल्या ण셍रीक्षिाोंच्या आधारे आम्ही उदमाोंजरातील (Paradoxurus hermaphroditus) वेगळ्या रोंगस्व셂पाची 셍 ोंद करत आह त. द ꅍीों ण셍रीक्षिाोंमधील उदमाोंजरात पाठीवरील तपणकरी भाग, पायाोंच्या खालच्या भागात काळ्या रोंगाची कमतरता आणि अोंदाजे Associate editor: शेपटीच्या अर्ध्ाा भागात पाोंढ앍या रोंगाचे साधर्म्ा णदसू셍 आले . या ण셍रीक्षिाोंमर्ध्े 셍 ोंदवण्यात आलेली उदमाोंजराोंची P S Jothish रोंगसोंगती णह साधारितः णदसू셍 येिा앍या उदमाोंजरापेक्षा वेगळी आहे.
    [Show full text]
  • Date Conducted: Interviewer: Location/ Name of Longhouse: Total Number of Doors in Longhouse
    Date conducted: Interviewer: Location/ Name of longhouse: Total number of doors in longhouse: Questionnaire (association between natural resources and local community) The purpose of this questionnaire is to obtain some information about the natural resource utilization by the local community. It will only take a couple of minutes to complete, and the results will be used as part of research done to understand the relationship between natural resources and its surrounding. It would be very helpful if you could give us some information about yourself to help us put your answers in context. General questions Age: Gender: □ male □ female Race: □ Iban □ Kayan □ Kenyah □ Penan □ Punan □ Bidayuh □ Kedayan □ Lun Bawang □ Others: ___________________ Religion: □ Christianity □ Muslim □ Buddhism □ Hinduism □ Folk religions □ Unaffiliated □ Others: __________________ Size of household: □ 1-2 □ 3-4 □ 5-6 □ >6 (normal days) □ 1-5 □ 6-10 □ 11-15 □ >15 (holidays/festive seasons) Occupation/ daily activities: Education level: □ Primary □ Secondary □ Tertiary □ Never attended school Household income: □ < RM500 □ RM500-1000 □ RM1001-1500 □>RM1500 Monthly expenses: □ < RM100 □ RM101-500 □ RM501-1000 □>RM1000 Questions Q1 Name the commonly and uncommonly found animals are that being hunt in nearby forest area (in native language if possible). No. Name of animals common uncommon Local name 1 Sambar deer 2 Muntjac 3 Mouse-deer 4 Bearded pig 5 Clouded leopard 6 Marble cat 7 Flat-headed cat 8 Leopard cat 9 Bay cat 10 Mongoose 11 Banded palm civet 12 Banded linsang
    [Show full text]
  • Ecosystem Services Certification Document for Ratah Timber, Long Hubung Sub-District, Ulu Mahakam District, East Kalimantan
    Forest Stewardship Council® Ecosystem Services Programme March 2017 Ecosystem Services Certification Document for Ratah Timber, Long Hubung sub-district, Ulu Mahakam District, East Kalimantan Part I: Information regarding the demonstration of impact Declaration of the ecosystem services for which a claim is being or will be made (Step 1) Please state the ecosystem service(s) for which you are making or plan to make FSC claims for the maintenance and/or enhancement of ecosystem services. You can choose more than one option. Carbon sequestration and storage Watershed services Biological diversity conservation Soil conservation Recreational services Management objectives related to maintenance and/or enhancement of each declared ecosystem service (Step 1) Biodiversity To maintain and protect terrestrial mammal and bird species. – 1 of 21 – FSC International Center GmbH · https://ic.fsc.org · FSC® F000100 Charles de Gaulle Strasse 5 · 53113 Bonn · Germany T +49 (0) 228 367 660 · F +49 (0) 228 367 66 30 Geschäftsführer | Director: Dr Hans-Joachim Droste Handelsregister | Commercial Register: Bonn HRB12589 Chosen ecosystem services impact to be demonstrated1 (Step 4) Biodiversity: Maintenance of native species or genetic diversity 1 Please define a theory of change for each chosen ecosystem service impact. You can use as many arrows and boxes for management activities, outputs, and outcomes as you need. FSC-PRO-30-006 V1-0 EN DEMONSTRATING THE IMPACT OF FOREST STEWARDSHIP ON ECOSYSTEM SERVICES – 2 of 21 – Theory of change template (Step 5) MANAGEMENT ACTIVITIES OUTPUTS OUTCOMES IMPACT Around 300–400 ha replanted Replanting trees after harvesting with native/local species Protecting habitat in HCV forests 12,080 ha HCV area protected Species inventory – all Maintenance Monitoring species via camera traps species including rarity and Species included in of native endangered status the inventory are species or maintained genetic diversity Cut only >40 cm (HP); >50 cm (HPT) of diameter.
    [Show full text]
  • Viverra Tangalunga) and Other Civets in Logged and Unlogged Lowland Dipterocarp Rain Forests in Sabah, Borneo
    City University of New York (CUNY) CUNY Academic Works Publications and Research Kingsborough Community College 2012 Notes on the Diet of the Malay Civet (Viverra tangalunga) and other Civets in Logged and Unlogged Lowland Dipterocarp Rain Forests in Sabah, Borneo Christina P. Colon Kingsborough Community College John B. Sugau How does access to this work benefit ou?y Let us know! More information about this work at: https://academicworks.cuny.edu/kb_pubs/44 Discover additional works at: https://academicworks.cuny.edu This work is made publicly available by the City University of New York (CUNY). Contact: [email protected] Malayan Nature Journal 2012, 64(1), 69-74 Short Note Notes on the Diet of the Malay Civet (Viverra tangalunga) and other Civets in Logged and Unlogged Lowland Dipterocarp Rain Forests in Sabah, Borneo CHRISTINA P. COLON1 and JOHN B. SUGAU Civet diets were examined in a logged and unlogged Bornean rain forest. Malay civets (Viverra tangalunga) consumed invertebrates, fruit, rodents, insectivores, birds, snakes and lizards, and appear to show preference for centipedes and scorpions. Other civet species consumed fruit, such as figs, Connarus sp. and Annona sp., particularly in the unlogged forest, but also consumed invertebrates and vertebrates. Reduced fruit consumption observed in the logged forest may be due to lower availability and may be offset by increased consumption of invertebrates. The increased overlap in diet between Malay civets and other civets in disturbed areas may lead to increased competition. Keywords: diet, frugivory, civet (Viverridae), logging, dipterocarp rain forest, Sabah, Borneo Scat and stomach content were used to compare diets of civets in logged and unlogged forest in the Danum Valley Conservation Area and Ulu Segama Forest Reserve in Sabah, Borneo.
    [Show full text]
  • 990 PART 23—ENDANGERED SPECIES CONVENTION Subpart A—Introduction
    Pt. 23 50 CFR Ch. I (10–1–01 Edition) Service agent, or other game law en- 23.36 Schedule of public meetings and no- forcement officer free and unrestricted tices. access over the premises on which such 23.37 Federal agency consultation. operations have been or are being con- 23.38 Modifications of procedures and nego- ducted; and shall furnish promptly to tiating positions. such officer whatever information he 23.39 Notice of availability of official re- may require concerning such oper- port. ations. Subpart E—Scientific Authority Advice (c) The authority to take golden ea- [Reserved] gles under a depredations control order issued pursuant to this subpart D only Subpart F—Export of Certain Species authorizes the taking of golden eagles when necessary to seasonally protect 23.51 American ginseng (Panax domesticated flocks and herds, and all quinquefolius). such birds taken must be reported and 23.52 Bobcat (Lynx rufus). turned over to a local Bureau Agent. 23.53 River otter (Lontra canadensis). 23.54 Lynx (Lynx canadensis). 23.55 Gray wolf (Canis lupus). PART 23—ENDANGERED SPECIES 23.56 Brown bear (Ursus arctos). CONVENTION 23.57 American alligator (Alligator mississippiensis). Subpart A—Introduction AUTHORITY: Convention on International Sec. Trade in Endangered Species of Wild Fauna 23.1 Purpose of regulations. and Flora, 27 U.S.T. 1087; and Endangered 23.2 Scope of regulations. Species Act of 1973, as amended, 16 U.S.C. 23.3 Definitions. 1531 et seq. 23.4 Parties to the Convention. SOURCE: 42 FR 10465, Feb. 22, 1977, unless Subpart B—Prohibitions, Permits and otherwise noted.
    [Show full text]
  • Conservation Programmes, Zoological Society of London, Regents Park, London, NW1 4RY CONTENTS
    PIGS, PALMS, PEOPLE AND TIGERS SURVIVAL OF THE SUMATRAN TIGER IN A COMMERCIAL LANDSCAPE 2003 ANNUAL REPORT BY T.M.MADDOX, E.GEMITA, S.WIJAMUKTI, A.SELAMPASSY, JAMBI TIGER PROJECT Conservation Programmes, Zoological Society of London, Regents Park, London, NW1 4RY CONTENTS SUMMARY 5 INTRODUCTION 7 The importance of commercial landscapes and oil palm 7 Tigers and oil palm 8 The need for conservation action in commercial landscapes 8 PROJECT GOALS AND OBJECTIVES 9 FUNDING AND SUPPORT 11 STUDY AREA BACKGROUND 12 PT Asiatic Persada 12 The ZSL / AP conservation collaboration 12 Location 12 Habitat types 13 METHODS 15 Camera trapping 15 Line transects 16 Secondary sign sureys 17 Capture-mark-recapture 18 Prey damage assessment 20 Tiger capture methods 21 Remote dart gun 21 Leg-hold traps 21 SURVEY EFFORT 23 Camera trapping 23 Line transects 24 Secondary sign surveys 24 Capture-mark-recapture 24 2 Prey damage assessment 24 Tiger capture methods 24 OBJECTIVE 1: ESTABLISHMENT OF PROJECT INFRASTRUCTURE 25 ZSL research team members 25 Collaborations and partnerships 25 PT Asiatic Persada 25 KSDA Jambi 25 PT Asialog 25 Local residents 25 Other organisations 26 Training 26 Data management 26 Field logistics 27 Objective summary 27 OBJECTIVE 2: SPECIES DIVERSITY AND ABUNDANCE IN AND AROUND OIL PALM 28 Species diversity 28 Species distribution and abundance 30 Objective summary 33 OBJECTIVE 3: PREY POPULATION BIOLOGY 35 Prey availability within the study area 35 Prey Diversity 35 Prey abundance 35 Impact on the plantation 38 Objective summary 38 OBJECTIVE 4: TIGER POPULATION AND RANGING ECOLOGY 40 Tiger population estimate 40 Camera trapping rates 40 Individual recognition 41 Effect of Camera trapping method 44 Ranging patterns 45 Objective summary 49 FUTURE WORK 50 3 REFERENCES 51 APPENDIX 53 Problems with “Camtrakker” camera traps 53 4 SUMMARY A key strategy for ensuring the survival of the Sumatran tiger is to work on their survival outside the protected area system.
    [Show full text]
  • Terrestrial Mammal Community Richness and Temporal Overlap Between Tigers and Other Carnivores in Bukit Barisan Selatan National Park, Sumatra
    Animal Biodiversity and Conservation 43.1 (2020) 97 Terrestrial mammal community richness and temporal overlap between tigers and other carnivores in Bukit Barisan Selatan National Park, Sumatra M. L. Allen, M. C. Sibarani, L. Utoyo, M. Krofel Allen, M. L., Sibarani, M. C., Utoyo, L., Krofel, M., 2020. Terrestrial mammal community richness and temporal overlap between tigers and other carnivores in Bukit Barisan Selatan National Park, Sumatra. Animal Biodi- versity and Conservation, 43.1: 97–107, DOI: https://doi.org/10.32800/abc.2020.43.0097 Abstract Terrestrial mammal community richness and temporal overlap between tigers and other carnivores in Bukit Barisan Selatan National Park, Sumatra. Rapid and widespread biodiversity losses around the world make it important to survey and monitor endangered species, especially in biodiversity hotspots. Bukit Barisan Selatan National Park (BBSNP) is one of the largest conserved areas on the island of Sumatra, and is important for the conservation of many threatened species. Sumatran tigers (Panthera tigris sumatrae) are critically endangered and serve as an umbrella species for conservation, but may also affect the activity and distribution of other carnivores. We deployed camera traps for 8 years in an area of Bukit Barisan Selatan National Park (BBSNP) with little human activity to document the local terrestrial mammal community and investigate tiger spatial and temporal overlap with other carnivore species. We detected 39 mammal species including Sumatran tiger and several other threatened mammals. Annual species richness averaged 21.5 (range 19–24) mammals, and re- mained stable over time. The mammal order significantly affected annual detection of species and the number of cameras where a species was detected, while species conservation status did not.
    [Show full text]
  • An Oil Palm Landscape
    an oil palm landscape Inda D. Solina1, Wilson Novarino2, Rizaldi1 and Anthony J. Giordano3 1 2 3S.P.E.C.I.E.S., Ventura, California, USA Corresponding author: Inda D. Solina; As of 2010, approximately 55,000km2 species richness at camera-traps, most likely because these species had become isolated in forest surrounded by completely and more plantation st August, 2018. Accepted 20th August, 2018 14 landscape to small carnivores, as well as what role species perceive roads, monoculture and open and competition in altered landscapes, as well areas as barriers to their movement and dispersal Asia are heavily dependent on intact tropical Neofelis diardi Pardofelis marmorata Study Area km Prionailurus bengalensis original standing vegetation along watercourses thereby contribute to species persistence across what degree corridors are important to smaller mammalian carnivores in tropical Asian landscapes, Sumatra, many species may occur sympatrically across large regions and thus occupy the same areas Camera trapping 15 Figure 1 relationship between species richness and various l For ambiguous and Figure 2 16 habitat characteristics and covariates, including relative sapling and tree density, canopy cover, Paradoxurus hermaphroditus were the only species detected in all three habitat Habitat characteristics Arctictis binturong Hemigalus derbyanus not detected in Arctogalidia trivirgata location constituted a central point encompassed civet were the only two species recorded in the Activity patterns marten, this species is known to be predominantly Table 1. The species, English name and local name, number of independent photos, habitat and IUCN status for the small Species Common name Local name #Photos % IUCN Mustelidae Musang leher kuning 1 2.86 F Viverridae Small-toothed palm civet Musang Akar 1 2.86 R Bearcat/Binturong Binturong 1 2.86 F VU Banded palm civet Musang Belang 20 F NT Masked palm civet Musang Galing 1 2.86 CF Common palm civet 20 F,CF,R Malay civet Musang Tenggalong 4 11.43 F Total 35 100 Figure 3.
    [Show full text]
  • Download Download
    PLATINUM The Journal of Threatened Taxa (JoTT) is dedicated to building evidence for conservaton globally by publishing peer-reviewed artcles OPEN ACCESS online every month at a reasonably rapid rate at www.threatenedtaxa.org. All artcles published in JoTT are registered under Creatve Commons Atributon 4.0 Internatonal License unless otherwise mentoned. JoTT allows unrestricted use, reproducton, and distributon of artcles in any medium by providing adequate credit to the author(s) and the source of publicaton. Journal of Threatened Taxa Building evidence for conservaton globally www.threatenedtaxa.org ISSN 0974-7907 (Online) | ISSN 0974-7893 (Print) Communication An updated checklist of mammals of Odisha, India Subrat Debata & Himanshu Shekhar Palei 26 July 2020 | Vol. 12 | No. 10 | Pages: 16219–16229 DOI: 10.11609/jot.6025.12.10.16219-16229 For Focus, Scope, Aims, Policies, and Guidelines visit htps://threatenedtaxa.org/index.php/JoTT/about/editorialPolicies#custom-0 For Artcle Submission Guidelines, visit htps://threatenedtaxa.org/index.php/JoTT/about/submissions#onlineSubmissions For Policies against Scientfc Misconduct, visit htps://threatenedtaxa.org/index.php/JoTT/about/editorialPolicies#custom-2 For reprints, contact <[email protected]> The opinions expressed by the authors do not refect the views of the Journal of Threatened Taxa, Wildlife Informaton Liaison Development Society, Zoo Outreach Organizaton, or any of the partners. The journal, the publisher, the host, and the part- Publisher & Host ners are not responsible
    [Show full text]
  • 42916-014: Sarulla Geothermal Power
    Environmental and Social Monitoring Report Safeguard and Social Monitoring Report Appendix G – Biodiversity Monitoring 2016 (Monitoring period: July – December 2016) June 2018 INO: Sarulla Geothermal Power Prepared by Sarulla Operations Limited for the Asian Development Bank. This safeguard and social monitoring report is a document of the borrower. The views expressed herein do not necessarily represent those of ADB's Board of Directors, Management, or staff, and may be preliminary in nature. In preparing any country program or strategy, financing any project, or by making any designation of or reference to a particular territory or geographic area in this document, the Asian Development Bank does not intend to make any judgments as to the legal or other status of any territory or area. Biodiversity Monitoring 2016 SOL Geothermal Project Area, North Tapanuli, North Sumatra Camera trapping and Primate Surveys A picture of a female sambar deer (Rusa unicolor), listed as Vulnerable on the IUCN Red List and protected species under Indonesian law, but still heavily hunted throughout Sumatra, caught on camera trap at SOL. 27th of November 2016 by PanEco/Yayasan Ekosistem Lestari requested by Sarulla Operations Ltd. Executive Summary Biodiversity monitoring is an integral part of the Biodiversity Action Plan (BAP) that was developed as part of a large-scale geothermal development project in North Tapanuli, North Sumatra, Indonesia. Baseline surveys were carried out between November 2013-June 2014 by Yayasan Ekosistem Lestari [camera trapping, primate and wildlife surveys, reptile and amphibian surveys] and a team of experts looking at vegetation and bird diversity. This report discusses the results of repeat biodiversity surveys focusing on camera trapping [3rd March-14 August 2016] and specific primate surveys [25 July-16 August 2016] in the forest area where Sarulla Operations Limited (SOL) is developing a large-scale geothermal project in/adjacent to the protected Batang Toru forest complex.
    [Show full text]